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The	role	of	behaviour	in	the	transition	to	more	energy	
efficient	use	at	home	–	Lessons	from	Portugal	
	
	
Ana	Sofia	Torres	Faria	
MBA	in	International	Industrial	Management	from	the	Esslingen	University	of	Applied	Science	(DE,	2003)	
‘European	Degree	in	International	Management’	(DEMI)	from	the	University	of	Valenciennes	et	du	Hainaut-
Cambresis	(FR,	2002)	
Degree	in	International	Management	from	the	RSM	Erasmus	University	(NL,	2001)	
Degree	in	Economics	from	the	Universidade	do	Minho	(PT,	2001)	
	
Thesis	submitted	in	partial	fulfilment	of	the	requirements	for	the	degree	of	a	Doctor	of	Philosophy	
December	2014	
	
	
Engineering	and	Innovation	Department	
Faculty	of	Mathematics,	Computing	and	Technology	
The	Open	University
I	
Abstract	
This	study	investigated	domestic	energy	use	behaviours	in	Portugal	and	ways	of	reducing	energy	use.	This	is	
important	 because	 current	 energy	 use	 in	 the	 developed	 world	 is	 considered	 to	 be	 unsustainable.	
Intervention	strategies	could	play	an	important	role	to	reduce	energy	use.	While	some	previous	research	
has	demonstrated	that	certain	intervention	strategies	did,	or	did	not,	produce	changes	in	behaviour,	they	
mostly	 could	 not	 sufficiently	 explain	 the	 underlying	 and	 impacting	 determinants,	 or	 how	 change	 came	
about	and	led	to	the	desired	adoption,	whether	short	or	long-term,	of	more	energy	efficient	behaviours.		
This	study	therefore	aims	to	explore	how	the	adoption	of	more	energy	efficient	behaviours	at	home	could	
be	encouraged.	With	this	the	research	has	the	objective	to	better	understand	the	different	determinants	of	
energy	use	at	home,	the	underlying	motivations,	barriers	and	potential	intervention	strategies.	To	achieve	
this	the	study	uses	an	exploratory	and	iterative	multi-method	approach	consisting	of	survey	questionnaires,	
followed	by	qualitative	research	through	focus	groups	targeted	at	energy	users	at	home,	and	also	individual	
in-depth	interviews	with	energy	conservation	intervention	practitioners.	
The	findings	of	this	research	show	that	if	the	rate	of	adoption	of	more	energy	efficient	behaviours	is	to	
increase,	then	interventions	that	are	focusing	on	providing	information	or	financial	incentives,	are	unlikely	
to	work	for	a	large	proportion	of	energy	users.	Instead,	the	adoption	of	more	energy	efficient	behaviours	at	
home	is	seen	to	depend	on	the	ability	of	intervention	strategies	to	challenge	existing	norms,	thus	creating	
new	understandings,	expectations	and	utilization	of	energy	services	that	could	manifest	in	the	adoption	of	
more	energy	efficient	behaviours.	With	this	findings	also	suggest	that	community-based	initiatives	might	be	
an	adequate	means	to	challenge	social	norms	and	to	bring	about	change.
II	
Declaration	
	
	
This	is	to	certify	that:	
	
The	 thesis	 comprises	 only	 my	 original	 work	 towards	 the	 PhD	 except	 where	 indicated,	 due	
acknowledgements	have	been	made	in	the	text	to	all	other	material	used,	the	thesis	is	less	than	100,000	
words	in	length,	inclusive	of	all	footnotes,	bibliographies	and	appendices.	
	
	
	
	
_____________	
Ana	Faria	
December	2014
III	
Acknowledgments	
First	and	foremost	I	would	like	to	thank	my	partner	in	life	Andreas	for	challenging	me	at	first	and	supporting	
me	afterwards	from	the	very	beginning	of	my	journey	until	today.	I	would	like	to	extend	my	gratitude	to	my	
parents	 who	 on	 their	 singular	 way	 have	 always	 supported	 me	 throughout	 these	 years.	 My	 PhD	 journey	
started	out	of	a	passion	for	the	area	I	work	in	and	the	vast	number	of	on-going	open	questions	to	explore.	
Having	 said	 that,	 I	 would	 like	 to	 thank	 the	 Open	 University	 and	 Professor	 Joaquim	 Borges	 Gouveia,	
President	of	the	board	of	Energaia,	for	the	opportunity	provided	by	granting	me	the	right	and	flexibility	to	
carry	 out	 my	 PhD	 work	 within	 a	 joint	 enterprise	 /	 academic	 partnership.	 I	 would	 like	 to	 extend	 my	
acknowledgement	to	my	current	and	former	work	colleagues,	in	particular	to	the	2	Js	(João	and	José)	for	
their	support,	and	for	all	the	fruitful	talks	and	companionships.		
With	regards	to	the	actual	body	of	this	work	I’d	like	to	express	my	gratitude	to	the	Entidade	Reguladora	do	
Sector	Energético	(ERSE)	for	selecting	the	Energyprofiler	project	for	funding,	which	supported	my	research	
at	its	initial	stage.	It	was	within	the	scope	of	this	project	that	I	had	the	pleasure	to	work	together	with	a	
highly	 skilled	 and	 motivated	 team	 and	 to	 learn	 how	 to	 become	 a	 researcher	 through	 practice.	 This	
collaboration	brought	up	a	number	of	opportunities	that	would	have	been	difficult	to	realize	otherwise.	The	
Energyprofiler	project	provided	me	with	the	opportunity	to	explore	the	topic	on	a	larger,	national	scale	that	
otherwise	would	have	been	difficult	to	achieve.	The	project	also	allowed	me	to	work	together	with	Dalila	
Antunes	and	Rui	Gaspar,	who	were	that	patient	to	walk	me	through	the	initial	SPSS	steps	and	with	time	
became	long-term	colleagues.	I’d	also	like	to	express	my	gratitude	to	those	FG	participants	and	individual	
interviewees,	who	I	shall	not	name,	but	who	worked	with	me	together	on	my	research	and	dedicated	parts	
of	their	time	to	answer	my	questions	and	allowed	me	to	proceed	with	my	research.	A	special	thank	you	to	
André,	who	took	part	of	this	research,	and	with	whom	unfortunately	I	will	not	be	able	to	share	this	work.	
Last,	but	not	least,	I	would	like	to	thank	Dr	Christian	Atkins,	Dr	Nii	Amoo	and	Dr	Kieran	Mervyn	who	have	
worked	as	external	reviewers	and	proof	readers.	
Finally	 I	 would	 like	 to	 thank	 my	 supervisors,	 Dr	 Christine	 Thomas,	 Dr	 Emma	 Dewberry	 and	 initially	 also	
Professor	Marylyn	Carrigan	who	supported	me	in	the	initial	phase,	as	well	as	the	wider	MCT	team	for	the	
support	and	guidance	provided	to	me.
IV	
Table	of	contents	
ABSTRACT	..................................................................................................................................................	I	
DECLARATION	...........................................................................................................................................	II	
ACKNOWLEDGMENTS	..............................................................................................................................	III	
TABLE	OF	CONTENTS	................................................................................................................................	IV	
LIST	OF	FIGURES	........................................................................................................................................	X	
LIST	OF	TABLES	........................................................................................................................................	XII	
LIST	OF	TERMINOLOGY	AND	ABBREVIATIONS	.........................................................................................	XIII	
1	 INTRODUCTION	..................................................................................................................................	1	
1.1	 ENERGY	USE	AND	SUSTAINABILITY	.................................................................................................................	1	
1.2	 MOTIVATIONS	AND	BARRIERS	TO	ENERGY	USE	.................................................................................................	3	
1.3	 ENERGY	USE	AND	BEHAVIOUR	CHANGE	..........................................................................................................	5	
1.4	 AIM	OF	THE	RESEARCH	...............................................................................................................................	6	
1.5	 RESEARCH	QUESTIONS	...............................................................................................................................	7	
1.6	 RESEARCH	PROCESS	AND	INFORMATION	FLOW	................................................................................................	8	
1.6.1	 Research	process	...........................................................................................................................	8	
1.6.2	 Information	flow	............................................................................................................................	9	
1.7	 THE	RESEARCH	WITHIN	THE	PORTUGUESE	CONTEXT	........................................................................................	11	
2	 ENERGY	USE	AND	SUSTAINABILITY	...................................................................................................	15	
2.1	 DOMESTIC	ENERGY	USE	............................................................................................................................	15	
2.1.1	 Invisibility	of	energy	use	..............................................................................................................	18	
2.1.2	 Energy	use	and	energy	saving	at	home	.......................................................................................	19	
2.2	 DETERMINANTS	OF	ENERGY	USE	AT	HOME	....................................................................................................	20	
2.2.1	 Social	and	cultural	influences	......................................................................................................	21	
2.2.2	 Comfort,	convenience	and	needs	.................................................................................................	23	
2.2.3	 Norms	and	energy	efficiency	.......................................................................................................	23	
2.2.4	 Economic	influences	....................................................................................................................	25
V	
2.2.5	 Income	levels	and	energy	poverty	...............................................................................................	26	
2.2.6	 Demographic	trends	....................................................................................................................	27	
2.2.7	 The	role	of	infrastructure	and	technological	factors	in	influencing	energy	use	at	home	............	28	
2.2.8	 The	rebound	effect	and	its	influence	on	determining	energy	use	at	home	.................................	29	
2.3	 CONCLUDING	REMARKS	............................................................................................................................	31	
3	 ENERGY	USE	BEHAVIOURS:	MOTIVATIONS	AND	BARRIERS	...............................................................	33	
3.1	 MOTIVATIONS	FOR	SAVING	ENERGY	AT	HOME	...............................................................................................	33	
3.2	 PRO-ENVIRONMENTAL	CONCERN:	A	MOTIVATIONAL	VARIABLE	OR	BARRIER	TO	BEHAVIOUR?	...................................	33	
3.3	 BARRIERS	TO	ADOPTING	MORE	ENERGY	EFFICIENT	BEHAVIOURS	........................................................................	37	
3.3.1	 Monetary	focus	as	a	barrier	........................................................................................................	37	
3.3.2	 External/macro	barriers:	policy	based,	structural	and	economic	barriers	...................................	37	
3.3.3	 Knowledge	based	barriers	...........................................................................................................	39	
3.3.4	 Cultural	–	normative	and	social	barriers	.....................................................................................	40	
3.4	 INDIVIDUAL	PSYCHOLOGICAL	BARRIERS	........................................................................................................	40	
3.4.1	 Habits	as	a	barrier	.......................................................................................................................	41	
3.4.2	 Comfort	as	a	psychological	barrier	..............................................................................................	41	
3.4.3	 Individual	beliefs	and	self-efficacy	as	a	barrier	............................................................................	42	
3.4.4	 Resistance	and	unwillingness	to	change	as	a	barrier	..................................................................	44	
3.5	 CONCLUDING	REMARKS	............................................................................................................................	45	
4	 ENERGY	USE	AND	INTERVENTION	STRATEGIES	.................................................................................	48	
4.1	 ENERGY	USE,	INTERVENTIONS	AND	SUPPORTIVE	FRAMEWORKS	.........................................................................	49	
4.1.1	 Potential	intervention	layers	.......................................................................................................	53	
4.2	 BEHAVIOURAL	CHANGE,	COMMUNICATION	AND	PERSUASION	...........................................................................	54	
4.2.1	 Persuasion	and	communication	..................................................................................................	57	
4.2.2	 Mental	models	and	communication	............................................................................................	58	
4.2.3	 Behavioural	change,	and	relevant	and	supportive	communication	............................................	59	
4.3	 STRUCTURAL	INTERVENTIONS	....................................................................................................................	59	
4.3.1	 Financial-economic	interventions	................................................................................................	60	
4.3.2	 Physical/technical	interventions	..................................................................................................	60
VI	
4.3.3	 Legal	regulation	...........................................................................................................................	60	
4.4	 PSYCHOLOGICAL	INTERVENTIONS	................................................................................................................	61	
4.4.1	 Information	provision	..................................................................................................................	62	
4.4.2	 Commitment	and	goal	setting	.....................................................................................................	65	
4.4.3	 Behavioural	intervention	through	design	....................................................................................	66	
4.4.4	 Rewards	and	punishments	..........................................................................................................	67	
4.4.5	 Learning	theories	and	modelling	.................................................................................................	69	
4.4.6	 Social	learning	community	based	approaches	............................................................................	70	
4.5	 COMBINED	STRUCTURAL/PSYCHOLOGICAL	INTERVENTIONS	.............................................................................	71	
4.5.1	 Prompting	strategies	...................................................................................................................	71	
4.5.2	 Feedback	provision	......................................................................................................................	72	
4.5.3	 Monitoring	systems	and	metering	...............................................................................................	73	
4.5.4	 Social	marketing	..........................................................................................................................	74	
4.6	 CONCLUDING	REMARKS	............................................................................................................................	77	
5	 RESEARCH	METHODOLOGY	AND	DESIGN	..........................................................................................	79	
5.1	 LITERATURE	REVIEW	ON	AVAILABLE	METHODS	...............................................................................................	80	
5.1.1	 Inductive	or	deductive	.................................................................................................................	80	
5.1.2	 Subjective	or	objective	.................................................................................................................	81	
5.1.3	 Positivism	or	constructivism	........................................................................................................	81	
5.1.4	 Qualitative	or	quantitative	..........................................................................................................	82	
5.1.5	 Available	research	instruments	...................................................................................................	84	
5.1.5.1	 Surveys	and	survey	questionnaires	......................................................................................................	85	
5.1.5.2	 Thematic	analysis	..................................................................................................................................	85	
5.1.5.3	 Content	analysis	...................................................................................................................................	86	
5.1.5.4	 Comparative	analysis	............................................................................................................................	86	
5.1.5.5	 In-depth	individual	interviews	..............................................................................................................	86	
5.1.5.6	 Telephone	interviews	...........................................................................................................................	86	
5.1.5.7	 Grounded	theory	..................................................................................................................................	87	
5.1.5.8	 Action	research	.....................................................................................................................................	88	
5.1.5.9	 Focus	groups	.........................................................................................................................................	88
VII	
5.1.5.10	 Direct	participant	observation	............................................................................................................	89	
5.2	 METHODS	USED	......................................................................................................................................	90	
5.3	 SURVEY	QUESTIONNAIRE	...........................................................................................................................	93	
5.3.1	 Survey	questionnaire	and	data	analysis	methodology	................................................................	94	
5.3.2	 Question	added	for	the	specific	purpose	of	this	research	work	...................................................	96	
5.4	 FOCUS	GROUPS	.......................................................................................................................................	98	
5.4.1	 Focus	group	objectives	................................................................................................................	99	
5.4.2	 Focus	group	composition	...........................................................................................................	101	
5.5	 IN-DEPTH	INDIVIDUAL	INTERVIEWS	............................................................................................................	104	
5.5.1	 Interview	objectives	...................................................................................................................	104	
5.5.2	 Sampling	of	interviewees	...........................................................................................................	105	
5.6	 SUMMARY	OF	EMPIRICAL	STUDY	METHODS	.................................................................................................	106	
5.7	 QUALITATIVE	DATA	ANALYSIS:	FOCUS	GROUP	AND	IN-DEPTH	INDIVIDUAL	INTERVIEWS	.........................................	107	
5.8	 RESEARCH	ETHICS	..................................................................................................................................	108	
5.9	 SUMMARY	...........................................................................................................................................	109	
6	 EXPLORING	DOMESTIC	ENERGY	USE	...............................................................................................	111	
6.1	 CHARACTERISTICS	OF	DOMESTIC	ENERGY	USE	..............................................................................................	111	
6.1.1	 Invisibility	as	a	distinctive	characteristic	of	energy	use	.............................................................	111	
6.1.2	 The	fundamental	role	of	domestic	energy	use	..........................................................................	116	
6.2	 DETERMINANTS	OF	DOMESTIC	ENERGY	USE	................................................................................................	116	
6.2.1	 Relation	of	behaviour	and	energy	use	.......................................................................................	117	
6.2.2	 Building	characteristics	..............................................................................................................	121	
6.2.3	 Growing	number	of	home	appliances	........................................................................................	121	
6.2.4	 Energy	efficient	home	appliances	and	overall	energy	prices	.....................................................	122	
6.2.5	 The	evolution	of	cultural	and	social	norms	................................................................................	125	
6.3	 CONCLUDING	REMARKS	..........................................................................................................................	127	
7	 FACTORS	INFLUENCING	ENERGY	USE	AT	HOME	..............................................................................	135	
7.1	 MOTIVATIONAL	VARIABLES	AND	ENERGY	EFFICIENT	BEHAVIOURS	....................................................................	135	
7.1.1	 The	motivation	for	saving	money	..............................................................................................	135
VIII	
7.1.2	 Pro-environmental	behaviour	and	pro-social	motivations	........................................................	137	
7.1.3	 Needs	and	expectations	and	its	relation	to	motivation	for	saving	energy	................................	144	
7.2	 BARRIERS	FOR	ADOPTING	MORE	ENERGY	EFFICIENT	BEHAVIOURS	.....................................................................	144	
7.2.1	 External/macro	barriers:	policy	based,	structural	and	economic	barriers	.................................	145	
7.2.2	 Knowledge	based	barriers	.........................................................................................................	147	
7.2.3	 Cultural-normative-social	barriers	.............................................................................................	152	
7.3	 INDIVIDUAL	PSYCHOLOGICAL	FACTORS	AS	A	BARRIER	.....................................................................................	154	
7.3.1	 Habits	as	an	obstacle	to	the	adoption	of	more	energy	efficient	behaviours	.............................	154	
7.3.2	 Comfort	and	convenience	..........................................................................................................	157	
7.3.3	 Efficacy	and	outcome	expectations	...........................................................................................	158	
7.3.4	 Resistance	to	and	unwillingness	to	change	...............................................................................	161	
7.4	 CONCLUDING	REMARKS	..........................................................................................................................	163	
8	 INTERVENTION	STRATEGIES	AND	PERCEIVED	EFFECTIVENESS	.........................................................	170	
8.1	 COMMUNICATION	DESIGN	AND	PERSUASION	..............................................................................................	171	
8.2	 STRUCTURAL	INTERVENTIONS	..................................................................................................................	173	
8.2.1	 Rewards	and	punishments	........................................................................................................	173	
8.2.2	 Incentives	and	samples	..............................................................................................................	174	
8.2.3	 Labelling	....................................................................................................................................	175	
8.2.4	 Demonstrating	and	facilitating	.................................................................................................	177	
8.2.5	 Intervention	through	design	......................................................................................................	178	
8.3	 PSYCHOLOGICAL	INTERVENTIONS	..............................................................................................................	179	
8.3.1	 Targeted	face-to-face	information	............................................................................................	179	
8.3.2	 Information	and	communication	campaigns	............................................................................	180	
8.3.3	 Education	interventions	.............................................................................................................	183	
8.3.4	 Community	based	interventions	................................................................................................	184	
8.4	 COMBINED	STRUCTURAL/PSYCHOLOGICAL	INTERVENTIONS	............................................................................	185	
8.4.1	 Information,	feedback	and	monitoring	equipment	...................................................................	185	
8.4.2	 Smart	metering	and	prompting	strategies	................................................................................	187	
8.4.3	 Information,	feedback	and	energy	bills	.....................................................................................	188
IX	
8.5	 CONCLUDING	REMARKS	..........................................................................................................................	188	
9	 CONCLUSION	..................................................................................................................................	196	
9.1	 SPECIFIC	ANSWERS	TO	THE	RESEARCH	QUESTIONS	........................................................................................	196	
9.1.1	 RQ1:	What	explains	energy	use	at	home?	.................................................................................	196	
9.1.2	 RQ2:	What	influences	energy	use	at	home?	..............................................................................	197	
9.1.3	 RQ3:	What	is	the	potential	role	of	intervention	strategies	on	energy	use	at	home?	................	199	
9.2	 KEY	FINDINGS	.......................................................................................................................................	200	
9.2.1	 Importance	to	challenge	the	understanding	of	normal	.............................................................	201	
9.2.2	 Invisibility	of	energy	and	its	implications	...................................................................................	202	
9.2.3	 Financial	motivations	to	save	energy	........................................................................................	202	
9.2.4	 Knowledge,	competence	and	self-efficacy	.................................................................................	203	
9.2.5	 Energy	efficient	behaviour	and	outcome	efficacy	......................................................................	203	
9.3	 LIMITATIONS	OF	THE	RESEARCH	................................................................................................................	204	
9.4	 SUGGESTED	FUTURE	RESEARCH	................................................................................................................	204	
REFERENCES	..........................................................................................................................................	206	
APPENDICES	..........................................................................................................................................	226	
APPENDIX	I:	ENERGYPROFILER	SURVEY	QUESTIONNAIRE	..........................................................................................	226	
APPENDIX	II:	REDUCED	VERSION	-	FG	QUESTIONNAIRE	BEFORE	DISCUSSION	................................................................	234	
APPENDIX	III:	CONSUMER	INTERVIEW	ROADMAP	...................................................................................................	235	
APPENDIX	IV:	PRACTITIONER	INTERVIEW	ROADMAP	...............................................................................................	238	
APPENDIX	V:	LIST	OF	ANSWERS	FOR	QUESTION	6	OF	EP	SURVEY	QUESTIONNAIRE	REGARDING	ENERGY	SAVING	REPORTED	
BEHAVIOURS	..................................................................................................................................................	240	
APPENDIX	VI:	–	LIST	OF	ANSWERS	FOR	QUESTION	15	OF	EP	SURVEY	QUESTIONNAIRE	REGARDING	ENERGY	SAVING	REPORTED	
BEHAVIOURS	..................................................................................................................................................	241	
APPENDIX	VII:	VARIABLES	DEFINED	DURING	ENERGYPROFILER	STUDY	.........................................................................	242	
APPENDIX	VIII:	–	LIST	OF	ANSWERS	FOR	QUESTION	Q16	OF	EP	SURVEY	QUESTIONNAIRE	(REPORTED	BARRIERS	AND	
CONSTRAINTS)	................................................................................................................................................	243	
APPENDIX	IX:	–	LIST	OF	IDENTIFIED	BARRIERS	DURING	THE	FG	.................................................................................	244	
APPENDIX	X:	–	SAMPLE	DISTRIBUTION	WITH	REGARD	TO	REGION,	GENDER,	AGE	GROUPS	AND	RURAL/URBAN	AREA	............	245
X	
	List	of	Figures	
FIGURE	1-1:	THE	THREE	MAIN	PILLARS	OF	SUSTAINABLE	DEVELOPMENT:	ECONOMIC	GROWTH,	ENVIRONMENTAL	PROTECTION	AND	
SOCIAL	EQUALITY,	(KENNEDY,	2011).	.................................................................................................................	2	
FIGURE	1-2:	THE	RELATION	BETWEEN	INDIVIDUAL	ENERGY	RELATED	BEHAVIOUR	AND	BARRIERS	TO	CHANGE,	(BARENERGY,	2011).
	...................................................................................................................................................................	4	
FIGURE	1-3:	SCHEMATIC	REPRESENTATION	OF	RESEARCH	DESIGN.	....................................................................................	8	
FIGURE	1-4:	SCHEMATIC	REPRESENTATION	OF	INFORMATION	FLOW.	...............................................................................	10	
FIGURE	2-1:	DISTRIBUTION	OF	ENERGY	CONSUMPTION	IN	HOUSEHOLDS	BY	SOURCE	TYPE	IN	2010,	(INE,	2011;	INE	I.P./DGEG,	
2011).	.......................................................................................................................................................	17	
FIGURE	2-2:	DISTRIBUTION	OF	ENERGY	CONSUMPTION	IN	HOUSEHOLDS	BY	USE	TYPE	IN	2010,	(INE	I.P./DGEG,	2011).	........	18	
FIGURE	2-3:	MAIN	FACTORS	INFLUENCING	CONSUMER	BEHAVIOUR	AND	EMERGENCE	OF	CONSUMPTION	PRACTICES,	(EEA,	2013).
	.................................................................................................................................................................	20	
FIGURE	2-4:	AN	ACTOR-STRUCTURE	MODEL	OF	CONSUMPTION,	(ADAPTED	FROM	SPAARGAREN	AND	VAN	VLIET	(2000)).	.......	22	
FIGURE	3-1:	DIAGRAMMATIC	REPRESENTATION	OF	THE	CONDITIONAL	RELATIONS	BETWEEN	EFFICACY	BELIEFS	AND	OUTCOME	
EXPECTANCIES	(ADAPTED	FROM	BANDURA	(1977B),	P.	350).	...............................................................................	43	
FIGURE	4-1:	REDUCING	CAR	USE:	FACTORS	AFFECTING	BEHAVIOURAL	CHANGE,	(PRENDERGRAST	ET	AL.	2008,	P.	104).	...........	50	
FIGURE	4-2:	DIAGRAMMATIC	REPRESENTATION	OF	THE	4E’S	MODEL,	(DEFRA,	2008,	P.	53).	............................................	52	
FIGURE	4-3:	MINDSPACE’S	INFLUENCES	ON	BEHAVIOUR,	(DOLAN,	2010).	......................................................................	52	
FIGURE	4-4:	THE	RELATION	BETWEEN	MATERIAL,	SOCIAL	AND	INDIVIDUAL	CONTEXTS,	ADAPTED	FROM	SOUTHERTON	ET	AL.	
(2011).	......................................................................................................................................................	53	
FIGURE	4-5:	THE	RELATION	BETWEEN	ENERGY	USE	DETERMINANTS,	MOTIVATIONS,	BARRIERS	TO	CHANGE	AND	TYPES	OF	
INTERVENTION,	ADAPTED	FROM,	(BARENERGY,	2011).	........................................................................................	54	
FIGURE	5-1:	RESEARCH	DESIGN	FROM	INITIAL	FRAMING	TO	IMPLEMENTATION.	.................................................................	79	
FIGURE	7-1:	AVERAGE	VALUES	FOR	RISK	PERCEPTION	OF	CLIMATE	CHANGE	AND	ATTITUDE,	KNOWLEDGE	AND	ENVIRONMENTAL	
BEHAVIOUR	[N=1.014,	F	(2.89	,	2914.70)	=	434.73,	P	=	.000,	Η
2	
=.57],	(ENERGYPROFILER,	2011).	....................	139	
FIGURE	7-2:	VALUES	FOR	ATTITUDE,	KNOWLEDGE	AND	RESPONSIBILITY	TOWARDS	ENERGY	USE	[N=1.014;	F	(2.89	,	2914.70)	=	
434.73,	P	=	.000,	Η
2	
=.57],	(ENERGYPROFILER,	2011).	...................................................................................	140	
FIGURE	7-3:	REPORTED	PRO-ENVIRONMENTAL	BEHAVIOURS	[N=1.014],	(ENERGYPROFILER,	2011).	.................................	141	
FIGURE	7-4:	REASONS	FOR	NOT	SAVING	ENERGY	AT	HOME	–	RESPONSES	FROM	FGS	........................................................	145	
FIGURE	7-5:	FREQUENCY	OF	CATEGORY	GROUPS	OF	BARRIERS	DURING	FGS.	...................................................................	145
XI	
FIGURE	7-6:	ENERGY	EFFICIENT	BEHAVIOURS	DISCUSSED	DURING	THE	FGS.	....................................................................	151	
FIGURE	8-1:	TYPE	OF	INTERVENTIONS	IN	RELATION	TO	THE	BARRIERS	THAT	COULD	BE	ADDRESSED.	......................................	170
XII	
List	of	Tables	
TABLE	5-1	–	FOCUS	GROUP	ROADMAP	AND	TECHNIQUES	USED.	...................................................................................	100	
TABLE	5-2	–	SUMMARY	OF	RESEARCH	ACTIVITIES.	.....................................................................................................	106	
TABLE	5-3	–	CONTENT	ANALYSIS.	...........................................................................................................................	108	
TABLE	6-1	–	RELATION	IN	BETWEEN	CHAPTER	AND	RESEARCH	QUESTIONS.	.....................................................................	111	
TABLE	6	-2	–	REPORTED	ENERGY	EFFICIENT	BEHAVIOURS	[N=1.014],	(ENERGYPROFILER,	2011).	......................................	119	
TABLE	6-3	–	SUMMARY	OF	FINDINGS	RELATING	TO	RQ1	............................................................................................	128	
TABLE	7-1	–	COMPOSITE	SCALES	[N=1.014,	F	(2.89	,	2914.70)	=	434.73,	P	=	.000,	Η2	=.57],	(ENERGYPROFILER,	2011)..
	.......................................................................................................................................................................	138	
TABLE	7-2	–	SUMMARY	OF	FINDINGS	RELATING	TO	RQ2.	...........................................................................................	164	
TABLE	8-1	–	SUMMARY	OF	FINDINGS	RELATING	TO	RQ3	............................................................................................	193
XIII	
List	of	Terminology	and	Abbreviations	
Attitudes:	“relatively	enduring	predisposition	to	respond	favourably	or	unfavourably”	towards	something,	
(Simons,	1976,	p.	80)	influencing	consumption	patterns,	recommendation	to	others,	beliefs	and	intentions”,	
(Schiffman	&	Kanuk,	1999,	pp.	199-200)	
Attitude-Behaviour	 Gap:	 positive	 attitudes	 do	 not	 necessarily	 lead	 to	 behaviour,	 (Kollmuss	 &	 Agyeman,	
2002),	 a	 phenomenon	 also	 known	 within	 pro-environmental	 behaviours,	 since	 general	 positive	 pro-
environmental	attitudes	do	not	seem	to	be	particular	important	predictors	of	environmentally	significant	
behaviour,	(Bamberg,	2003;	Poortinga,	Steg,	&	Vlek,	2004;	Schultz,	Oskamp,	&	Mainieri,	1995;	Thøgersen,	
2004).	
Behaviour:	the	result	of	multiple	conscious	and	unconscious	processes	as	well	as	internal	(psychological	
variables	such	as	norms,	beliefs	or	values)	and	external	variables	(e.g.	social,	economic	physical),	drivers	and	
constraints,	personal	capabilities,	or	habits	and	routines,	(Jackson,	2005;	Nye,	Whitmarsh,	&	Foxon,	2010;	
Stern,	2000).	
Behavioural	change	intervention:	Generic	and	specific	interventions	to	support	a	change	in	behaviour	at	
the	individual	and	population	level.	In	the	environmental	context	it	can	be	understood	as	a	change	in	the	
patterns	of	consumption	of	resources,	(Committee	on	Climate	Change	[CCC],	2012).	
Behaviour-Based	 Programs:	 Energy	 efficiency	 programs	 that	 utilize	 an	 understanding	 of	 how	 individuals	
interact	 with	 energy	 in	 order	 to	 decrease	 energy	 demand,	 (American	 Council	 for	 an	 Energy-Efficient	
Economy	[ACEEE],	n.d.).	
Beliefs:	psychological	state	in	which	an	individual	holds	a	proposition	or	premise	to	be	true,	(Schwitzgebel,	
2010),	which	in	terms	of	behaviour	could	be	the	“salient	information,	relevant	to	the	behaviour”,	(Ajzen,	
1991,	p.	189).	
Biocapacity:	the	area	of	land	and	productive	oceans	actually	available	to	produce	renewable	resources	and	
absorb	CO2	emissions,	(World	Wide	Fund	for	Nature	[WWF],	2012).	Biocapacity	quantifies	nature’s	capacity	
to	produce	renewable	resources,	provide	land	for	built-up	areas	and	provide	waste	absorption	services	such	
as	carbon	uptake.	Biocapacity	acts	as	an	ecological	benchmark	against	which	the	Ecological	Footprint	can	be
XIV	
compared.	Both	the	Ecological	Footprint	and	biocapacity	are	expressed	in	a	common	unit	called	a	global	
hectare,	where	1	gha	represents	a	biologically	productive	hectare	with	world	average	productivity.		
CID:	For	the	purpose	of	this	research	CID	stands	for	‘Consumer	Interview’	meaning	the	3	interviews	that	
were	 performed	 to	 consumers	 selected	 from	 the	 focus	 group	 that	 had	 been	 performed	 as	 part	 of	 the	
empirical	study.	
Collective	efficacy:	“sense	of	collective	efficacy”	does	exist	where	individuals	can	solve	their	problems	and	
improve	their	lives	through	concerted	effort,	(Bandura,	1986,	p.	449).	
Comprehensive	 Home	 Energy	 Audits:	 An	 assessment	 of	 a	 home’s	 energy	 use	 that	 includes	 a	 visual	
inspection,	 diagnostic	 testing,	 analysis,	 and	 a	 list	 of	 proposed	 improvements,	 ending	 with	 guidance	 to	
complete	the	work,	or	actual	completion	of	the	work,	(ACEEE,	n.d.).	
Concept,	conception	or	construct:	abstract	object,	or	a	mental	representation,	e.g.	wellbeing,	depression,	
poverty,	achievement,	family.	They	are	not	only	the	building	blocks	of	theory,	but	they	also	form	the	link	
between	theory	and	empirical	research,	(Bergman,	2010).	
Consumerism:	emphasis	on	or	preoccupation	with	the	acquisition	of	consumer	goods,	(Oxford	University	
Press,	2013).	
Consumption:	 the	 “human	 transformation	 of	 materials	 and	 energy”,	 (Royal	 Society	 of	 London	 &	 U.S.	
National	Academy	of	Sciences,	1997,	p.	684),	requiring	the	“selection,	use,	disposal,	and	recycling	of	goods	
and	services”,	(Campbell,	1995,	p.	102).	
Curtailment	 behaviours:	 behaviours	 that	 must	 be	 performed	 frequently,	 involving	 repetitive	 efforts	 to	
reduce	 energy,	 and	 involve	 more	 operational	 day	 to	 day	 habits	 and	 routines,	 such	 as	 lowering	 the	
thermostat,	 turning	 lights	 and	 appliances	 off,	 (Abrahamse,	 Steg,	 Vlek,	 &	 Rothengatter,	 2005;	 Gardner	 &	
Stern,	2002).	
Demand-Side	Management:	The	planning,	implementation,	and	monitoring	of	utility	activities	designed	to	
encourage	consumers	to	modify	patterns	of	electricity	usage,	including	the	timing	and	level	of	electricity	
demand,	(U.S.	Energy	Information	Agency	[EIA],	2013).
XV	
Descriptive	norm:	what	most	people	do;	the	perception	individuals	hold	about	what	is	normal	in	a	given	
situation,	(Cialdini,	Kallgren,	&	Reno,	1991;	Cialdini,	Reno,	&	Kallgren,	1990).	
Dwelling:	a	self-contained	unit	of	accommodation,	(Department	for	Communities	and	Local	Government	
[DCLG],	2012).	
Ecological	Footprint:	tracks	humanity’s	demands	on	the	biosphere	by	comparing	humanity’s	consumption	
against	the	Earth’s	regenerative	capacity,	or	biocapacity,	by	calculating	the	area	required	to	produce	the	
resources	 people	 consume,	 the	 area	 occupied	 by	 infrastructure,	 and	 the	 area	 of	 forest	 required	 for	
sequestering	 CO2	 not	 absorbed	 by	 the	 ocean,	 (Galli	 et	 al.,	 2007;	 Kitzes	 et	 al.,	 2009;	 Wackernagel	 et	 al.,	
2002).	
Efficacy	expectations:	“the	conviction	that	one	can	successfully	execute	the	behaviour	required	to	produce	
outcomes”,	(Bandura,	1977a,	p.	193).	
Efficiency	behaviours:	infrequent	type	of	behaviours,	like	for	example	one-off	actions,	which	often	entail	an	
investment,	such	as	loft	or	cavity	wall	insulation,	or	buying	an	energy	efficient	air	conditioner.	Commonly	
also	referred	to	as	‘efficiency	behaviours’	or	‘investment	behaviours’,	(Abrahamse	et	al.,	2005;	Gardner	&	
Stern,	2002;	Kempton,	Boster,	&	Hartley,	1995).	
Energy	Audit:	assessment	of	a	home's	energy	use.	These	include	a	number	of	different	types	of	surveys,	
including	 (in	 increasing	 order	 of	 cost	 and	 complexity):	 online	 audits,	 in-home	 home	 energy	 surveys,	
diagnostic	home	energy	surveys,	and	comprehensive	home	energy	audits,	(ACEEE,	n.d.).	
Energy	 Conservation:	 reduction	 in	 the	 amount	 of	 energy	 consumed	 in	 a	 process	 or	 system,	 or	 by	 an	
organization	or	society,	through	economy,	elimination	of	waste,	and	rational	use,	(BusinessDictionary,	n.d.).	
Saving	energy	by	doing	with	less	or	doing	without	(e.g.,	setting	thermostats	lower	in	winter	and	higher	in	
summer;	turning	off	lights;	taking	shorter	showers;	turning	off	air	conditioners;	etc.),	(ACEEE,	n.d.).	
Energy	efficiency:	ratio	of	‘useful’	outputs	to	energy	inputs	for	a	system.	The	system	in	question	may	be	an	
individual	energy	conversion	device	(e.g.	a	boiler),	a	building,	an	industrial	process,	a	firm,	a	sector	or	an	
entire	 economy,	 (Sorrell,	 2007).	 Percentage	 of	 total	 energy	 input	 to	 a	 machine	 or	 equipment	 that	 is	
consumed	in	useful	work	and	not	wasted	as	useless	heat,	(BusinessDictionary,	n.d.).
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Energy	 efficiency	 gap:	 difference	 between	 the	 ‘actual	 energy	 efficiency’	 and	 the	 ‘potential	 efficiency’,	
meaning	 part	 of	 the	 efficiency	 gain	 due	 to	 technological	 developments	 is	 being	 ‘taken	 back’,	 (Feenstra,	
Backhaus,	&	Heiskanen,	2009).	
Energy	Efficiency	Measure:	particular	good	or	practice	that	provides	an	energy	efficiency	benefit.	Upgraded	
insulation,	 energy	 efficient	 appliances,	 and	 adjusting	 a	 boiler’s	 limit	 control	 are	 examples	 of	 measures,	
(ACEEE,	n.d.).	
Energy	Efficiency	Potential:	amount	of	energy	savings	possible,	(ACEEE,	n.d.).	
Energy	 Management	 System:	 computerized	 system	 for	 fully	 automatic	 control	 of	 HVAC,	 lighting,	
refrigeration,	and	other	commercial	building	subsystems	in	order	to	accurately	manage	and	monitor	indoor	
temperature,	 comfort,	 and	 environmental	 quality.	 An	 EMS	 often	 saves	 energy	 and	 money	 by	 operating	
systems	only	when	needed	and	by	allowing	time-of-day	scheduling	and	peak	load	shedding	control,	(ACEEE,	
n.d.).	
Energy	services:	these	are	the	services	that	people	gain	from	using	energy	and	include	warm	rooms,	hot	
water,	a	well-lit	home	and	refrigerated	food,	(Environmental	Change	Institute	[ECI],	2005)	
Energy	 Performance	 Certificate	 (EPC):	 The	 certificate	 provides	 a	 rating	 for	 residential	 and	 commercial	
buildings,	showing	their	energy	efficiency	based	on	the	performance	of	the	building	itself	and	its	services	
(such	 as	 heating	 and	 lighting).	 EPCs	 are	 required	 whenever	 a	 building	 is	 built,	 sold	 or	 rented	 out,	 (CCC,	
2012).	
Environmentally	Significant	Behaviour	(ESB):	a	behaviour	that	does	not	“threaten	human	health,	welfare,	
or	other	things	people	value”,	(Stern,	1997,	p.	15)	and	that	is	characterized	by	its	“positive	impact	on	the	
availability	 of	 materials	 or	 energy	 from	 the	 environment	 and/or	 by	 the	 extent	 to	 which	 the	 behaviours	
positively	alter	the	structure	and	dynamics	of	ecosystems	or	the	biosphere”,	(Stern,	2000,	p.	408).	
EP:	For	the	purpose	of	this	research	EP	stands	for	‘energyprofiler	study’	as	had	been	conducted	within	the	
empirical	work.	
FG:	For	the	purpose	of	this	research	FG	stands	for	‘Focus	Group’	as	they	had	been	conducted	within	the	
empirical	work.
XVII	
Habits:	Even	though	this	work	is	aware	of	the	different	understanding	from	the	fields	of	psychology	and	
sociology	of	the	habits	construct,	it	is	not	within	the	scope	of	this	research	to	advocate	for	one	or	the	other	
understanding.	As	a	result	of	this,	habits,	routines	and	practices	might	be	used	interchangeably	meaning	
individuals	running	on	autopilot,	(Grist,	2010).	
Household:	one	person	or	a	group	of	people	who	have	the	accommodation	as	their	only	or	main	residence	
and	either	share	at	least	one	meal	a	day,	or	share	the	living	room,	(DCLG,	2012).	
Information-Behaviour	 Gap:	 disconnection	 between	 knowledge	 hold	 and	 behaviour	 outcome,	 (Jackson,	
2005;	Schultz,	2002;	Southerton,	McMeekin,	&	Evans,	2011;	Stern,	1999).	
Injunctive	social	norm:	what	ought	to	be	done;	explicitly	reflect	the	moral	rules	and	guidelines	of	the	social	
group,	(Cialdini	et	al.,	1990,	1991).	
Lifestyles:	the	way	people	live	their	life,	fulfil	their	needs	and	aspirations,	through	the	mediation	of	goods	
that	 are	 closely	 linked	 to	 material	 and	 resource	 flows,	 (Backhaus,	 Breukers,	 Mont,	 Paukovic,	 &	 Mourik,	
2012).	
Moral	norms:	an	altruistic	behaviour	results	once	a	moral	norm	is	activated.	This	activation	occurs	once	an	
individual	becomes	aware	that	his	or	her	behaviour	has	possible	negative	consequences	for	others	and	is	
willing	to	take	personal	responsibility	for	the	others’	well-being,	(Schwartz,	1970,	1977).	
Norms:	“rules	and	standards	that	are	understood	by	members	of	a	group	and	that	guide	and/or	constrain	
social	behaviour	without	the	force	of	laws”,	(Cialdini	&	Trost,	1998,	p.	152).	
Outcome	expectancy:	“a	person’s	estimate	that	a	given	behaviour	will	lead	to	certain	outcomes”,	(Bandura,	
1977a,	p.	193).	
Perceived	 Behavioural	 Control:	 individual’s	 belief	 about	 the	 easiness	 or	 difficulty	 of	 performing	 a	 given	
behaviour,	(Ajzen	&	Madden,	1986).	
Personal	Carbon	Alliances:	With	PCAs,	each	adult	has	an	equal	carbon	allocation	to	cover	purchases	of	gas,	
electricity,	petrol	and	aviation.	The	PCA	brings	home	to	the	individual,	in	a	forceful	way,	the	amount	of	
carbon	being	released	through	daily	activities,	(ECI,	2005).
XVIII	
Personal	 norms:	 feelings	 of	 strong	 moral	 obligation	 that	 people	 experienced	 to	 engage	 in	 pro-social	
behaviour,	(Schwartz,	1970,	1977).	
PID:	For	the	purpose	of	this	research	PID	stands	for	‘Provider	Interview’,	meaning	the	3	interviews	that	were	
performed	to	people	working	for	intervention	providers	within	the	energy	area.	
Price	elasticity:	the	percentage	change	in	one	variable	following	a	percentage	change	in	another,	holding	
other	variables	constant,	(Sorrell,	2007).	
Rebound	effect:	also	known	as	‘take-back	effect’,	is	measured	by	the	difference	between	the	projected	and	
actual	savings	due	to	increased	efficiency	and	is	normally	expressed	as	a	percentage	of	the	expected	energy	
savings	from	an	energy	efficiency	improvement,	(Sorrell,	2007).	
Self-efficacy:	“people’s	judgments	of	their	capabilities	to	organise	and	execute	courses	of	action	required	to	
attain	designated	types	of	performances”,	(Bandura,	1986,	p.	395).	
Single-Action	Bias:	tendency	people	have	to	engage	into	single	corrective	actions	and	therefore	‘doing	their	
bit’	thus	increasing	the	resistance	and	decreasing	the	need	of	taking	additional	actions,	(Weber,	1997).	
Smart	Meters:	An	advanced	electricity	meter	that	uses	real	time	sensors	to	provide	information	on	power	
consumption	and	price,	(ACEEE,	n.d.).	
Social	 Marketing:	 the	 application	 of	 marketing	 principles	 and	 tools	 to	 achieve	 socially	 desirable	 goals,	
(Andreasen,	1995;	Kotler	&	Zaltman,	1971).	
Social	Norms:	unwritten	rules	and	expectations	that	frame	appropriate	and	inappropriate	expectations	and	
behaviours	within	a	group	of	individuals,	(Lewis,	1969).	
Spillover	effect:	term	used	to	describe	the	transferability	across	behaviours	and	contexts	between	one	kind	
of	environmental	behaviour	and	another,	(Thøgersen	&	Ølander,	2002).	
Subjective	norm:	individual	perception	about	what	other	people	who	are	important	to	him/her	think	of	the	
specific	behaviour,	rather	than	the	individual	personal	belief	about	the	morality	of	the	given	behaviour,	
(Ajzen	&	Fishbein,	1980).
XIX	
Sustainable	 development:	 “the	 kind	 of	 development	 that	 meets	 the	 needs	 of	 the	 present	 without	
compromising	the	ability	of	future	generations	to	meet	their	own	needs”,	(United	Nations	[UN],	1987).	
Sustainable	consumption:	“the	use	of	goods	and	services	that	respond	to	basic	needs	and	bring	a	better	
quality	of	life,	while	minimising	the	use	of	natural	resources,	toxic	materials	and	emissions	of	waste	and	
pollutants	over	the	life	cycle,	so	as	not	to	jeopardise	the	needs	of	future	generations”,	(Norwegian	Ministry	
of	the	Environment,	1994).	
Values:	Considered	by	some,	as	the	hardest	thing	to	change,	(Andreasen,	1995;	Kotler,	Roberto,	&	Roberto,	
1989),	values	might	be	overall	defined	as	“a	desirable	trans-situational	goal	varying	in	importance,	which	
serves	as	a	guiding	principle	in	the	life	of	a	person	or	other	social	entity”,	(Schwartz,	1992,	p.	21).
1. Introduction	
	
1	
1 	Introduction	
Current	energy	use	in	the	developed	world	is	considered	to	be	unsustainable	with	energy	consumption	and	
production	 patterns	 undermining	 sustainable	 development	 and	 the	 equitable	 distribution	 of	 resources	
worldwide,	 (Intergovernmental	 Panel	 on	 Climate	 Change,	 [IPCC],	 2007;	 Stern,	 2007).	 To	 achieve	 more	
sustainable	energy	use	levels	requires	a	combination	of	cultural	and	technological	advances	and	innovation	
in	the	design	of	social	and	institutional	systems	and	systems	of	production	and	consumption,	(Cole,	2011).	
However,	although	such	changes	at	societal	level	are	likely	to	lead	to	some	reductions	in	energy	use	at	the	
household	 level,	 it	 is	 recognised	 that	 significant	 change	 in	 household	 energy	 consumption	 is	 unlikely	 to	
occur	without	changes	in	individuals’	energy	usage	behaviours.	To	achieve	the	goal	of	sustainable	levels	of	
household	energy	use	requires	a	clear	understanding	of	energy	use	at	home	and	what	influences	current	
energy	 use	 behaviours	 so	 to	 adopt	 more	 energy	 efficient	 behaviours,	 (Darby,	 2006;	 Janda,	 2011).	 This	
research	 aims	 to	 explore	 how	 the	 adoption	 of	 more	 energy	 efficient	 behaviours	 at	 home	 could	 be	
encouraged.	With	this	the	research	has	the	objective	to	better	understand	the	different	determinants	of	
energy	use	at	home,	the	role	of	motivations	and	barriers	that	drive	energy	use	at	home,	and	the	potential	
role	of	interventions	to	promote	behavioural	change.	
This	chapter	firstly	sets	the	context	for	the	research	by	describing	the	need	for	working	towards	a	more	
sustainable	 society	 and	 the	 important	 role	 that	 energy	 use	 plays	 in	 this.	 It	 then	 considers	 the	 role	 of	
individuals’	energy	use	behaviours;	what	motivates	them	and	what	barriers	they	face	and	how	they	might	
be	influenced	to	reduce	domestic	energy	use.		The	chapter	concludes	with	the	research	aims,	the	research	
questions	and	the	structure	of	the	thesis.	
1.1 	Energy	use	and	sustainability	
Energy	use	underpins	most	aspects	of	modern	life.	It	is	important	in	the	production	of	goods,	most	services	
and	the	way	we	live.	However,	many	forms	of	energy,	in	particular	fossil	fuels,	contribute	to	environmental	
problems,	 such	 as	 climate	 change	 and	 local	 air	 pollution,	 (Organization	 for	 Economic	 Co-operation	 and	
Development,	(OECD],	2012).	What	we	desire	in	a	modern	lifestyle	therefore	seems	to	come	at	the	cost	of	
undesired	environmental	problems	and	this	is	particularly	prevalent	for	developed	countries,	(UN,	1987;
1. Introduction	
	
2	
IPCC,	2007;	Stern,	2007).	Recent	trends	regarding	increasing	global	population,	(U.S.	Census	Bureau,	2011;	
UN,	2011)	and	increasing	material	consumption,	as	a	consequence	of	the	growing	level	of	perceived	needs,	
have	exacerbated	this	problem,	(The	Royal	Society,	2012).	It	has	therefore	been	argued	that	changes	in	
current	lifestyles	will	be	required	to	achieve	a	sustainable	level	at	which	the	needs	of	the	present	are	met	
without	 compromising	 the	 environment	 for	 future	 generations	 so	 as	 to	 allow	 for	 the	 long-term	 use	 of	
natural	resources	for	current	as	well	as	future	generations,	(Backhaus	et	al.,	2012;	IUCN,	UNEP,	&	WWF,	
1991;	 UN,	 1987).	 Development	 should	 thus	 be	 socially	 and	 morally	 just,	 ethically	 acceptable	 and	
economically	sound,	with	environmental	indicators	as	important	as	economic	indicators,	(Leal	Filho,	2011;	
UN,	1987).	As	such,	sustainable	development	implies	a	balanced	intersection	of	economic,	environmental	
and	social	factors,	(Elkington,	1997),	(Figure	1-1).		
	
Figure	1-1:	The	three	main	pillars	of	sustainable	development:	economic	growth,	environmental	protection	and	social	
equality,	(Kennedy,	2011).	
However,	 evidence	 suggests	 that	 it	 will	 become	 increasingly	 difficult	 to	 meet	 such	 expectations	 and	
commitments,	(WWF,	2012),	within	a	fast	growing	human	population	that	has	increased	from	1.6	billion	in	
1900	to	7	billion	in	2011,	(U.S.	Census	Bureau,	2011)	and	is	forecast	to	reach	just	over	9.3	billion	by	2050,	
(UN,	2007).	This	rapid	and	widespread	change	in	the	global	human	population,	coupled	with	unprecedented	
levels	of	consumption,	has	implications	for	finite	planetary	resources	and	presents	a	challenge	not	only	to	
the	environment,	but	also	to	human	health	and	wellbeing,	(The	Royal	Society,	2012).	What	citizens	from	
developed	countries	perceive	as	being	a,	‘normal	lifestyle’,	might	not	be	sustainable	in	a	global	context	of	
population	growth	and	depleting	natural	resources.	This	becomes,	in	particular,	apparent	when	considering	
the	 ecological	 footprint	 that	 measures	 the	 demands	 of	 humanity	 on	 the	 biosphere	 by	 comparing
1. Introduction	
	
3	
consumption	 against	 the	 Earth’s	 regenerative	 capacity,	 or	 biocapacity,	 (WWF,	 2012).	 The	 ecological	
footprint	shows	a	consistent	trend	of	overconsumption	for	the	few	last	decades,	with	a	growing	biocapacity	
deficit.	Humanity’s	annual	demand	on	the	natural	world	has	exceeded	what	the	Earth	can	annually	renew	
since	 the	 1970s.	 In	 2008	 it	 exceeded	the	Earth’s	biocapacity	by	more	than	50	per	cent,	which	means	it	
would	take	1.5	years	for	the	Earth	to	fully	regenerate	the	renewable	resources	consumed	in	one	year,	(Galli	
et	al.,	2007;	Kitzes	et	al.,	2009;	Poumanyvong	&	Kaneko,	2010;	Wackernagel	et	al.,	2002;	OnePlanetLiving,	
n.d.,	 WWF,	 2012).	 At	 the	 individual	 human	 level	 the	 ecological	 footprint	 is	 influenced	 by	 the	 choices	
individuals	make	on	what	they	eat,	what	products	they	purchase,	how	they	heat/cool	their	homes	and	how	
they	travel,	(WWF,	2012).	A	challenge	of	our	age	could	thus	be	seen	in	decoupling	human	progress	from	
resource	 use	 and	 environmental	 decline,	 (KPMG,	 2012).	 This	 is	 to	 say	 decoupling	 unsustainable	 human	
needs,	 wants	 and	 expectations	 and	 rebuilding	 these	 in	 a	 more	 sustainable	 way.	 As	 long	 as	 this	 is	 not	
achieved	however,	there	will	be	a	conflict	between	limitless	needs	vs.	limited	resources	and	the	need	to	
define	the	boundaries	of	what	is	understood	as	‘sustainable’,	‘normal’	or	‘socially	acceptable’	consumption,	
(Norwegian	Ministry	of	the	Environment,	1994;	UN,	1987,	1992).		
Sustainability	 in	 relation	 to	 energy	 use	 can	 also,	 “be	 understood	 as	 a	 continuous	 learning	 process	 that	
occurs	when	a	given	society	acquires	the	necessary	knowledge	to	reduce	its	energy	consumption	without	
diminishing	its	quality	of	life	or	creating	new	social	inequalities”,	(Tabara	et	al.,	1999,	p.	1).	Therefore	the	
focus	of	fulfilling	individual	needs	in	a	more	sustainable	way	is	a	core	concept	of	this	thesis;	reinforcing	that	
sustainability	in	energy	terms	should	not	mean	losing	wellbeing,	but	rather	doing	things	in	a	different	way.	
Part	of	that	different	way	requires	individual	behavioural	change	and	an	understanding	of	the	motivations	
and	barriers	for	change.	
1.2 	Motivations	and	barriers	to	energy	use	
Motivations	 are	 factors	 encouraging,	 or	 influencing,	 a	 change	 in	 behaviour,	 or	 maintaining	 a	 current	
behaviour	and	barriers	those	that	obstruct	or	limit	change.	Saving	money	and	protecting	the	environment	
are	the	first	and	second	most	frequently	reported	motivations	for	saving	energy	at	home,	(Eurobarometer,	
2011a).	However,	they	are	not	often	fully	realized	as	reduced	energy	use	might	be	perceived	as	negatively	
impacting	comfort	or	wellbeing.	In	such	an	equation	the	gain	and	motivation	of	maintaining	old	habits	can
1. Introduction	
	
4	
have	a	higher	priority	than	that	of	saving	money	and	protecting	the	environment.	In	this	situation	the	gain	
and	 motivation	 of	 maintaining	 old	 habits	 constitute	 a	 barrier	 to	 the	 adoption	 of	 more	 energy	 efficient	
lifestyles,	 (Jackson,	 2005;	 Prendergrast,	 Foley,	 Menne,	 &	 Isaac,	 2008).	 Individuals’	 own	 habits,	 or	 their	
compliance	to	existing	and	commonly	accepted	standards	and	social	norms,	can	work	as	motivations	to	
maintaining	existing	behaviours,	(EEA,	2013;	Shove,	2003).	To	achieve	a	change	towards	energy	efficient	
behaviour	 would	 thus	 require	 understanding	 the	 respective	 barriers,	 (Homans,	 1958),	 as	 well	 as	 the	
underlying	 attitudes	 and	 values,	 (Andreasen,	 1995;	 Homans,	 1958;	 Kotler	 et	 al.,	 1989).	 This	 interplay	
between	barriers	and	behaviours	is	depicted	in	Figure	1-2	and	Throne-Holst,	Strandbakken,	and	Stø	(2008)	
suggest	that	it	consists	of	six	barrier	groups.	Figure	1-2	highlights	the	interplay	in	terms	of	macro	and	micro	
factors	 between	 the	 individual,	 surrounding	 setting	 and	 infrastructure	 that	 could	 motivate,	 enable	 and	
reinforce	individual	behavioural	change	as	well	as	illustrate	the	complexity	of	such	relations.	
	
Figure	1-2:	The	relation	between	individual	energy	related	behaviour	and	barriers	to	change,	(Barenergy,	2011).	
In	 accordance	 with	 Throne-Holst	 et	 al.	 (2008),	 barriers	 toward	 the	 adoption	 of	 more	 energy	 efficient	
behaviours	could	be	grouped	as:	
(1) Information/knowledge	 barriers,	 where	 people	 are	 lacking	 relevant	 information	 regarding	 energy	
efficiency	measures	that	they	could	adopt.		
(2) Physical	and	structural	barriers,	where	the	existing	physical	structure	of	dwellings	and	of	society	can	be	
a	disincentive	and	tend	to	lock	people	into	less	sustainable	behaviours.
1. Introduction	
	
5	
(3) Political	 barriers,	 such	 as	 laws	 and	 regulations	 that	 frame	 and	 determine	 the	 ability	 to	 change	
individual	behaviours.		
(4) Cultural-normative	 barriers,	 as	 people	 do	 not	 live	 in	 isolation,	 and	 social	 and	 cultural	 norms	 may	
restrict	engagement	in	more	energy	efficient	behaviours,	even	if	they	hold	a	positive	opinion	towards	
them.		
(5) Economic	 barriers,	 since	 more	 energy	 efficient	 solutions	 can	 be	 expensive,	 the	 higher	 prices	 may	
therefore	discourage	people	from	becoming	more	efficient	in	their	energy	use.		
(6) Individual-psychological	 barriers,	 as	 a	 pre-determinant	 of	 the	 adoption	 of	 more	 energy	 efficient	
behaviours.	 This	 is	 the	 individual	 willingness	 to	 change	 behaviour	 that	 is	 influenced	 by	 individual’s	
personal	habits	and	comfort	zones,	including	for	instance	the	concept	of	self-efficacy,	(Bandura,	1986),	
or	Perceived	Behaviour	Control,	(Ajzen,	1991).		
As	such,	any	given	motivation	might	have	to	face	a	number	of	barriers	from	different	barrier	groups.	To	
achieve	behavioural	change	towards	the	adoption	of	more	energy	efficient	behaviours	therefore	would	not	
only	require	understanding	all	of	the	respective	barriers,	but	also	the	underlying	attitudes	and	values,	and	
subsequently	means	to	overcome	each	of	them.	
1.3 	Energy	use	and	behaviour	change	
Energy	saving	can	be	realized	through	infrastructural	development,	increasing	technological	development	
and	deployment,	the	introduction	of	more	energy	efficient	materials	and	appliances	and	also	through	the	
rational	and	sustainable	use	of	energy	at	home,	based	on	the	adoption	of	more	energy	efficient	behaviours.	
For	 decades,	 research	 has	 mainly	 focused	 on	 the	 technical	 component,	 such	 as	 providing	 more	 energy	
efficient	home	appliances	or	building	materials	and	only	more	recently	has	attention	been	directed	to	the	
non-technical	 components	 and	 to	 the	 contribution	 of	 how	 people	 behave	 and	 interact	 with	 home	
appliances	and	infrastructures,	in	terms	of	energy	use	at	home,	(EEA,	2013).	The	reasons	for	a	focus	on	
technology	might	have	been	that	it	was	expected	to	be	‘easier’	to	influence	efficiency	behaviours	that	are	
characterized	 by	 one-off	 actions,	 instead	 of	 changing	 curtailment	 behaviours,	 which	 must	 be	 performed	
frequently,	(Abrahamse	et	al.,	2005;	Gardner	&	Stern,	2002).	However,	focusing	on	efficiency	behaviours	
usually	involves	the	need	for	an	initial	investment,	which	can	itself	act	as	a	barrier.	But	even	in	the	event
1. Introduction	
	
6	
that	those	barriers	can	be	overcome	and	financial	savings	generated,	the	energy	saved	might	subsequently	
be	used	for	other	energy	using	activity,	or	to	increase	the	number	of	home	appliances	that	people	have.	It	
can	thus	lead	to	what	is	known	as	a	‘rebound-effect’	where	the	energy	saving	potential	is	not	realized	in	
practice,	(Khazzoom,	1980).	For	these	reasons	the	contribution	that	curtailment	behaviours	can	play	should	
not	be	underestimated	and	interventions	that	attempt	to	change	behaviours	must,	ultimately,	need	to	lead	
to	long-term	behaviour	change	to	be	successful.	The	literature	shows	a	diversity	of	existing	intervention	
strategies	 and	 types	 that	 could	 support	 and	 enable	 behavioural	 change	 and	 can	 be	 grouped	 into	 two	
broader	categories:	(a),	structural	and	(b),	psychological	interventions,	(Poortinga	et	al.,	2004;	Steg,	2003).	
Structural	interventions	aim	to	change	the	(social)	context	in	which	behavioural	decisions	take	place,	based	
on	the	belief	that	by	altering	the	conditions	on	which	behaviour	is	based,	the	behaviour	will	then	change	in	
accordance.	 In	 contrast,	 psychological	 interventions	 aim	 at	 changing	 existing	 perceptions,	 knowledge,	
attitudes,	norms	and	values,	(i.e.	individual,	micro-level	variables).	The	underlying	assumption	here	is	that	
by	 changing	 these	 determinants,	 behaviour	 will	 change	 accordingly.	 Structural	 and	 psychological	
interventions	have	been	employed	to	encourage	household	energy	conservation	with	varying	degrees	of	
success,	(Abrahamse	et	al.,	2005;	Geller,	Harrington,	Rosenfeld,	Tanishima,	&	Unander,	2006;	Heiskanen,	
Mourik,	 Feenstra,	 &	 Pariag,	 2009;	 Kurz,	 2002;	 Southerton	 et	 al.,	 2011).	 A	 number	 of	 studies	 apparently	
suggest	 that	 success,	 when	 it	 occurs,	 rarely	 survives	 when	 the	 change	 interventions	 are	 discontinued,	
(Abrahamse	et	al.,	2005;	Heiskanen	et	al.,	2009;	Kurz,	2002;	Lutzenhiser,	2002).	Despite	the	growing	body	of	
existing	research	and	evidence,	there	appears	however	still	to	be	no	clear	evidence	within	the	literature	on	
the	potential	long-term	effectiveness	of	change	interventions	within	the	field	of	energy	use	at	home;	an	
area	that	this	work	attempts	to	explore	further.	
1.4 	Aim	of	the	research	
The	overall	aim	of	this	research	is	to	explore	how	the	adoption	of	more	energy	efficient	behaviours	at	home	
could	be	encouraged.	Within	this,	a	first	objective	is	to	provide	an	overview	of	the	nature	of	energy	use	at	
home	 and	 the	 factors	 that	 influence	 energy	 use,	 (chapter	 2).	 Subsequently	 the	 research	 investigates	
whether	 the	 same	 set	 of	 factors	 and	 conditions	 can	 be	 found	 within	 the	 empirical	 study	 in	 Portugal,	
(chapter	6).	Secondly,	this	research	has	the	objective	to	advance	on	the	theory	of	motivating,	enabling	and
1. Introduction	
	
7	
reinforcing	 factors	 that	 could	 promote	 the	 adoption	 of	 more	 energy	 efficient	 habitual	 behaviours	 and	
practices	at	a	household	level,	(chapter	3),	as	well	as	for	the	Portuguese	context,	(chapter	7).	Thirdly,	this	
research	has	the	objective	to	explore	the	potential	effectiveness	of	change	interventions	within	the	field	of	
energy	use	at	home	and	the	different	types	of	interventions	that	might	be	used,	(chapter	4)	and	how	those	
are	perceived	and	evaluated	within	the	examples	of	practice	in	Portugal,	(chapter	8).	
The	reason	for	the	geographic	focus	of	this	research	was	two-fold.	Firstly,	the	researcher	was	aware	of	an	
apparent	scarcity	of	existing	studies	that	investigated	domestic	energy	use	in	Portugal	and	secondly,	for	
pragmatic	reasons,	as	the	researcher	is	based	in	Portugal	and	cognisant	of	the	social	context	of	household	
energy	use.	The	geographical	scope	has	been	limited	to	northern	Portugal	to	explore	the	topic	of	research	
in	more	depth.	
1.5 	Research	Questions		
Based	upon	the	review	of	the	literature	as	well	as	driven	by	the	thesis	aim	and	objectives,	the	following	
research	questions,	(RQ),	have	been	derived:	
Research	Question	1:	What	explains	energy	use	at	home?	
a) What	are	the	characteristics	of	energy	use	at	home?	
b) What	are	determinants	of	energy	use	at	home?	
c) How	do	individuals	understand	their	energy	use	at	home?	
Research	Question	2:	What	influences	energy	use	at	home?	
a) What	are	motivational	variables	for	adopting	more	energy	efficient	behaviours?	
b) What	are	the	barriers	for	adopting	more	energy	efficient	behaviours?		
c) How	do	individual	psychological	factors	influence	energy	use?	
Research	Question	3:	What	is	the	potential	role	of	intervention	strategies	on	energy	use	at	home?	
a) What	are	perceived	requirements	of	intervention	strategies?	
b) What	are	individual	perceptions	on	the	effectiveness	of	intervention	strategies?
1. Introduction	
	
8	
1.6 	Research	process	and	information	flow	
This	section	provides	an	overview	of	the	research	process	and	information	flow.	
1.6.1 	Research	process	
To	fully	explore	the	research	questions,	this	research	uses	a	mixed	methods	design,	where	qualitative	and	
quantitative	methods	are	combined.	The	use	of	both	qualitative	and	quantitative	methods	was	seen	to	be	
necessary	 to	 encompass	 differing	 aspects	 of	 the	 research,	 as	 explained	 in	 Chapter	 5.	 Figure	 1-3	 is	 a	
schematic	representation	of	the	research	design.	
	
Figure	1-3:	Schematic	representation	of	research	design.	
As	can	be	seen	in	Figure	1-3,	the	research	starts	with	a	comprehensive	literature	review	of	the	theoretical	
approaches	 to	 understanding	 human	 behaviour	 in	 general	 and	 more	 specifically,	 those	 concerned	 with	
more	 energy	 efficient	 lifestyles.	 To	 better	 explore	 the	 topic,	 the	 literature	 around	 energy	 use	 and	
sustainability	was	reviewed	to	locate	discussion	and	identify	the	reasons	why	people	are	expected	to	use	
less	energy	at	home.	In	addition,	the	literature	within	the	field	of	behavioural	change,	more	generally	as	
well	as	within	an	energy	context,	has	been	reviewed.	Chapter	2	explores	the	use	of	energy	at	a	household
1. Introduction	
	
9	
level	and	its	relation	to	sustainability.	Chapter	3	reviews	the	literature	on	understanding	human	behaviour	
and	in	particular,	of	energy	related	behaviours	at	home.	This	section	also	looks	at	motivating	factors	and	
barriers	related	to	individual	behavioural	change	within	the	energy	area.	Chapter	4	looks	at	the	potential	
effectiveness	 of	 change	 interventions	 within	 the	 field	 of	 energy	 use	 at	 home	 and	 the	 different	 types	 of	
interventions	that	might	be	applied.	This	chapter	includes	a	reflection	around	theories	of	persuasion	and	
their	role	in	frameworks	for	change	such	as	social	marketing.	Chapter	5	details	the	research	methodologies	
adopted	and	the	research	design	for	the	empirical	phase	of	this	research.	Chapter	6,	7	and	8	present	and	
discuss	 the	 findings	 from	 the	 empirical	 phase	 of	 this	 research.	 These	 include	 the	 results	 from	 the	
energyprofiler	national	survey,	exploratory	focus	groups	and	in-depth	interviews.	Finally,	chapter	9	presents	
the	research	conclusions,	drawing	on	the	theoretical	and	empirical	findings	and	discusses	the	contribution	
of	this	research.	
1.6.2 	Information	flow	
Figure	1-4	provides	a	schematic	representation	of	the	information	and	how	the	respective	chapters	and	
sections	inform	each	other.	As	can	be	seen,	in	Figure	1-4	there	are	three	direct	information	strings	that	start	
in	chapter	1,	(sections	1.1,	1.2,	1.3),	which	are	then	followed	up	in	the	literature	review,	(chapters	2,	3,	and	
4)	and	subsequently	looked	at	empirically,	(chapters	6,	7,	and	8).
1. Introduction	
	
10	
	
Figure	1-4:	Schematic	representation	of	information	flow.	
	
	 	
Chapter(1(*(Introduction
1.1.#Energy#use#and#
sustainability#
1.2.#Motivations#and#
barriers#to#energy#use
1.3.#Energy#use#and#
behaviour#change
Chapters(2,(3(and(4(*(Literature(Background(
2.#Energy#use#and#
sustainability
3.#Energy#use#behaviours:#
motivations#and#barriers
4.##Energy#use#and#
Intervention#strategies
Chapters(6,(7(and(8(*(Empirical(Work(
6.#Exploring#domestic#
energy#use#in#Portugal
7.#Factors#influencing#
energy#use#at#home
8.#Intervention#strategies#
and#perceived#
effectiveness
Chapter(9(*(Conclusion 9.2.1.#RQ1 9.2.2.#RQ2 9.2.3.#RQ3
RQ1:(What(explains(energy(use(at(home? X
RQ1a.#What#are#the#characteristics#of#energy#
use#at#home?
X
RQ1b.#What#are#determinants#of#energy#use#at#
home?
X
RQ1c.#How#do#individuals#understand#their#
energy#use#at#home?
RQ2:(What(influences(energy(use(at(home? X
RQ2a.#What#are#motivational#variables#for#
adopting#more#energy#efficient#behaviours?
X
RQ2b.#What#are#the#barriers#for#adopting#more#
energy#efficient#behaviours?#
X
RQ2c.#How#do#individual#psychological#factors#
influence#energy#use?
X
RQ3:(What(is(the(potential(role(of(intervention(
strategies(on(energy(use(at(home?
X
RQ3a.#What#are#perceived#requirements#of#
intervention#strategies?
X
RQ3b.#What#are#individual#perceptions#on#the#
effectiveness#of#intervention#strategies?
X
Thesis(information(flow
Relation(between(sections(and(Research(Questions((RQ,(section(1.5.)
Aim(of(the(research((section(1.4)
The#overall#aim#of#the#research#is#to#explore#how#the#adoption#of#more#energy#efficient#behaviours#at#home#could#be#
encouraged.#Chapter#2#aims#to#provide#an#overview#of#the#nature#of#energy#use#at#home#and#the#factors#that#influence#energy#
use#with#Chapter#6#investigating#whether#the#same#set#of#factors#and#conditions#can#be#found#within#the#empirical#study#in#
Portugal.#Chapter#3#aims#to#better#understand#the#motivating,#enabling#and#reinforcing#factors#that#could#promote#the#adoption#
of#energy#efficient#habitual#behaviours#and#practices#at#a#household#level,#while#Chapter#7#examines#if#similar#conditions#can#be#
found#in#the#Portuguese#context.#Chapter#4#explores#the#potential#effectiveness#of#change#interventions#within#the#field#of#
energy#use#at#home#and#the#different#types#of#interventions#that#might#be#used#and#subsequently#within#Chapter#8#how#those#
are#perceived#and#evaluated#within#the#examples#of#practice#in#Portugal.#
1. Introduction	
	
11	
1.7 The	research	within	the	Portuguese	context	
Previous	research	shows	that	structural	psychological	interventions	can	be	applied	to	support	and	enable	
behavioural	change	of	energy	use	at	home,	(Poortinga	et	al.,	2004;	Steg,	2003),	and	that	such	interventions	
have	 been	 employed	 with	 varying	 degrees	 of	 success,	 (Abrahamse	 et	 al.,	 2005;	 Geller,	 Harrington,	
Rosenfeld,	 Tanishima,	 &	 Unander,	 2006;	 Heiskanen,	 Mourik,	 Feenstra,	 &	 Pariag,	 2009;	 Kurz,	 2002;	
Lutzenhiser,	2002;	Southerton	et	al.,	2011).	Despite	the	growing	body	of	existing	research	and	evidence,	
there	 appears	 to	 be	 however	 a	 lack	 of	 clear	 evidence	 within	 the	 literature	 on	 the	 potential	 long-term	
effectiveness	of	such	interventions.	This	is	in	particular	true	for	studies	carried	out	in	Portugal.	This	lack	in	
existing	studies	within	Portugal	perhaps	results	from	the	fact	that	energy	consumption	has	only	recently	
become	a	matter	that	gained	in	importance.	It	thus	remains	unclear	whether	the	same	set	of	factors	and	
conditions	from	such	existing	studies	can	also	be	found	within	Portugal,	and	in	the	case	that	they	could	be	
found	how	effective	such	interventions	have	been	in	the	long-term.	
Having	remained	relatively	unchanged	during	the	period	from	2003	to	2008,	the	gross	inland	consumption	
of	energy	in	Portugal	decreased	by	5.7	%	in	2009,	and	much	of	this	change	is	claimed	to	not	be	a	result	of	a	
structural	 shift	 in	 the	 pattern	 of	 energy	 consumption,	 but	 that	 it	 can	 be	 attributed	 to	 a	 lower	 level	 of	
economic	activity	as	a	result	of	the	financial	and	economic	crisis,	(Eurostat,	2015).	Consumption	rebounded	
in	2010	in	most	of	the	Member	States	—	with	only	Lithuania,	Greece,	Portugal,	Cyprus,	Croatia	and	Spain	
recording	consecutive	contractions	in	consumption	in	2009	and	2010	—	possibly	reflecting	the	low	level	of	
economic	output	and	consumer	confidence	in	several	of	these	Member	States,	(Eurostat,	2015).	
Since	2012	this	situation	did	change	however	and	largely	impacted	by	EU	wide	regulations	and	initiatives,	
(Portuguese	Government,	2013).	As	a	result	of	this	the	National	Energy	Efficiency	Action	Plan	(NEEAP)	has	
been	 adopted	 in	 2008,	 and	 the	 National	 Renewable	 Energy	 Action	 Plan	 (NREAP)	 in	 2010,	 (Portuguese	
Government,	 2013).	 NEEAP	 and	 NREAP	 are	 both	 policy	 instruments	 aimed	 at	 achieving	 the	 targets	 and	
international	commitments	with	regard	to	energy	efficiency	and	the	use	of	energy	from	renewable	sources	
that	the	Portuguese	Government	had	agreed	to.	NEEAP	and	NREAP	are	part	of	a	policy	that	promotes	a	
rational	and	sustainable	energy	model,	without	compromising	the	competitiveness	of	enterprises	or	the	
quality	of	life,	programs	and	plans	that	annually	provide	strategic	guidelines	which	aim	to	contribute	to
1. Introduction	
	
12	
specific	objectives	and	to	allow	to	boost	measures	at	all	levels	(ADENE,	n.d.).	NEEAP	and	NREAP	also	aim	at	
identifying	existing	barriers,	to	support	improvement	of	energy	efficiency,	increase	in	energy	derived	from	
renewable	 sources	 and	 with	 a	 view	 to	 establishing	 the	 most	 suitable	 programmes	 and	 measures	 for	
complying	 with	 the	 said	 commitments,	 without	 neglecting	 national	 situation,	 (Portuguese	 Government,	
2013).		
Based	on	NEEAP	and	NREAP	policy	instruments	the	Regulatory	Authority	for	Energy	Services	(ERSE),	that	is	
responsible	for	the	definition	of	mechanisms	to	promote	energy	efficiency,	has	established	a	competitive	
mechanism	to	support	actions	for	demand	management	within	the	‘Plan	to	the	Promotion	of	Efficiency	in	
Electric	 Energy	 Consumption’	 (PPEC)	 program.	 PPEC	 aims	 to	 promote	 measures	 to	 improve	 efficiency	 in	
energy	consumption	through	actions	undertaken	by	suppliers,	network	operators	and	promotion	entities,	
and	that	are	targeted	at	a	number	of	market	segments,	(Portuguese	Government,	2013).	Such	measures	are	
divided	in	tangible	and	intangible	measures	and	according	to	the	following	three	market	segments:	industry	
and	agriculture;	trade	and	services;	and	the	residential	sector.	Within	the	tangible	measures	there	appeared	
to	be	a	predominance	of	lighting	measures	(including	public	lighting),	consumption	management	systems,	
or	 for	 electronic	 variable	 speed	 drives,	 (ERSE,	 2010).	 Within	 the	 intangible	 type	 of	 measures	 the	 most	
common	measures	related	to	the	dissemination	and	information	campaigns	targeted	at	a	household	level	
and	at	final	consumers,	but	also	to	energy	audits,	(ERSE,	2010).	
The	 interest	 in	 the	 funding	 available	 has	 been	 growing	 over	 the	 years	 with	 the	 2008	 call	 for	 projects	
receiving	131	projects	that	were	presented	by	21	promoters	and	equalling	a	total	amount	of	approximately	
56	million	euros	of	investment;	and	a	final	set	of	159	projects	presented	by	48	promoters	in	2011-2012	and	
equalling	a	total	amount	of	approximately	57.1	million	euros	in	funding,	(ERSE,	2007;	ERSE,	2009;	ERSE,	
2012).	From	this	initial	set,	a	selection	process	had	to	take	place	and	for	instance,	in	2011,	57	measures	
were	 approved	 and	 received	 funding	 within	 the	 national	 context.	 Among	 those,	 17	 projects	 were	
implemented,	 in	 the	 market	 segment	 ‘Domestic	 Energy’	 on	 three	 different	 settings:	 lighting	 (5),	
consumption	 management	 (9),	 and	 dissemination	 (3),	 (ERSE,	 n.d.).	 Two	 practical	 examples	 of	 such	
measures	are	described	in	the	following:	
a) ‘Save	 Electric	 Energy’:	 in	 2008	 the	 Portuguese	 Association	 for	 Consumer	 Protection	 (DECO)	
promoted	a	national	campaign	in	order	to	provide	information	on	the	meaning	of	saving	electric
1. Introduction	
	
13	
energy,	in	three	different	main	areas:	home,	work,	and	school.	For	this	purpose,	teams	made	up	of	
young	 graduates	 were	 formed	 –	 named	 “carbon	 brigades”,	 who	 acted	 throughout	 the	 country	
raising	awareness	by	awarding	promotional	material	(ERSE,	2008);	
	
b) ‘Guide	for	Energy	Efficiency’:	launched	in	2012	by	the	Portuguese	government,	directly	supported	by	
the	Portuguese	Agency	for	the	Energy	(ADENE).	This	guide	provided	practical	recommendations	and	
awareness-raising	 information	 regarding	 how	 to	 better	 use	 electric	 devices	 on	 a	 rational	 and	
sustainable	way,	in	diverse	contexts	such	as	while	using	household	appliances,	but	also	as	a	guide	to	
support	the	introduction	of	the	new	European	Union	Energy	Label	(ADENE,	2013).	
Apart	from	few	exceptions	most	of	the	intangible	projects	do	not	report	on	the	amount	of	energy	that	
could	be	saved	as	a	result	of	the	project	and	as	such	there	is	no	indicator	of	the	success	and	efficacy	of	the	
intervention.	
In	addition	to	those	programmes	and	measures,	the	Portuguese	government,	in	collaboration	with	ADENE,	
implemented	two	practical	support	financing	instruments:	the	Energy	Efficiency	Fund	(FEE)	and	the	Support	
Fund	for	Innovation	(FAI).	The	FEE	is	a	financial	instrument	that	aims	to	fund	programmes	and	measures	
under	 the	 NEEAP,	 to	 encourage	 energy	 efficiency	 for	 both	 enterprises	 and	 citizens,	 to	 support	 energy	
efficiency	projects,	and	to	promote	behavioural	change	in	this	domain,	through	cross-oriented	actions	of	
energy	 efficiency	 in	 the	 areas	 of	 behaviour,	 taxation	 and	 incentives,	 and	 funding,	 (FEE,	 n.d.).	 The	 FAI	
supports	 innovation	 and	 technological	 development	 projects,	 technology	 demonstration	 projects	 in	 the	
areas	of	renewable	energy	and	energy	efficiency,	investment	projects	in	energy	efficiency,	and	partnership	
building	support	services	between	Portuguese	companies	and	the	scientific	and	technological	system,	(FAI,	
n.d.).	With	this	Portugal	is	determined	to	achieve	the	national	energy	efficiency	general	target	for	2020	that	
aims	 to	 reduce	 primary	 energy	 use	 by	 25%,	 along	 with	 a	 specific	 target	 for	 Public	 Administration	 of	
achieving	a	reduction	of	30%	(European	Commission,	n.d.).	Portugal	also	aims	to	reduce	the	nation’s	energy	
dependence	and	safeguard	security	of	supplies,	by	promoting	a	balanced	energy	mix,	including	the	use	of	
energy	from	endogenous	renewable	sources	(Portuguese	Government,	2013).	
The	 energyprofiler	 study	 that	 supported	 parts	 of	 the	 empirical	 study	 presented	 in	 this	 thesis	 has	 been	
carried	 out	 within	 exactly	 this	 wider	 context.	 The	 energyprofiler	 study	 was	 a	 collaborative	 Portuguese
1. Introduction	
	
14	
national	funded	research	project	coordinated	by	the	author	of	this	research	on	behalf	of	Energaia,	a	local	
energy	agency	in	Vila	Nova	de	Gaia,	Portugal,	together	with	two	additional	project	partners,	Factor	Social	
and	Terrasystemics.	The	study	was	one	of	the	intangible	PPEC	measures	selected	in	the	2009	application	
round	and	aimed	at	defining	and	characterizing	the	Portuguese	population	in	segments/profiles	based	on	
the	 collected	 data	 regarding	 individual	 perceptions,	 attitudes,	 competence	 and	 patterns	 of	 energy	
consumption	 in	 the	 residential	 sector	 (Energaia,	 2008).	 These	 segments/profiles	 could	 later	 be	 used	 to	
support	the	development	of	more	specific	and	targeted	policies	and	interventions	in	order	to	improve	their	
efficacy	towards	reducing	energy	use	at	home.	The	motivation	for	the	project	was	an	identified	gap	in	the	
knowledge	 regarding	 national	 energy	 use	 patterns	 in	 the	 residential	 sector	 in	 Portugal,	 and	 the	 energy	
saving	 potential	 that	 could	 be	 derived	 from	 such	 consumption	 patterns	 (Energyprofiler,	 2011).	 The	
energyprofiler	 study	 thus	 attempted	 to	 explain	 what	 influences	 energy	 use	 at	 home	 and	 how	 could	 the	
population	be	segmented,	highlighting	the	major	differences	in	between	segments,	(Energyprofiler,	2011).		
Chapter	9	will	provide	further	information	on	how	the	findings	of	the	research	presented	in	this	thesis	do	
relate	to	the	national	context	as	has	been	described	within	this	section.
2. Energy	use	and	sustainability	
	
15	
2 	Energy	use	and	sustainability		
This	first,	of	three,	literature	review	chapters	provides	a	brief	introduction	to	the	subject	of	sustainability	
and	energy	use	in	the	home.	It	explores	the	literature	on	sustainability	aspects	and	the	characteristics	and	
determinants	 of	 domestic	 energy	 use	 and	 how	 lifestyles	 shape	 energy	 use,	 or	 negatively	 impact	 the	
sustainable	 use	 of	 it.	 Energy	 is	 essential	 for	 us	 to	 live	 the	 way	 we	 know.	 Even	 though	 improvements	in	
efficiency	 could	 have	 allowed	 OECD
1
	 countries	 to	 decouple	 GDP	 growth	 from	 growth	 in	 primary	 energy	
consumption,	(Geller	et	al.,	2006),	this	has	not	happened	and	energy	consumption	is	thus	still	closely	linked	
to	GDP	growth,	(Sorrell,	2007).	This	section	will	provide	an	overview	on	energy	consumption,	the	variables	
that	 are	 influencing	 energy	 consumption	 and	 opportunities	 for	 greater	 efficiencies	 within	 European	
households	in	general,	and	Portugal	in	particular.	
Chapter	3	further	explores	what	could	explain	energy	use	at	home,	with	a	particular	focus	on	motivations	
and	barriers	towards	the	adoption	of	more	energy	efficient	behaviours.	The	final	literature	review,	chapter	
4,	explores	how	the	adoption	of	more	energy	efficient	behaviours	could	be	potentially	encouraged.	
2.1 	Domestic	energy	use	
The	amount	of	energy	consumed	by	individuals	within	their	homes	accounts	for	a	significant	share	of	total	
energy	 consumption
2
	 and	 CO2	 emissions,	 (BPIE,	 2011;	 Deutsch,	 2010;	 Gardner	 &	 Stern,	 2002).	 In	 2009,	
European	households	were	responsible	for	68	percent	of	the	total	final	energy	use	in	buildings	and	25.4	
percent	 of	 total	 final	 energy	 was	 consumed	 by	 the	 residential	 sector	 in	 Europe	 in	 2008,	 (EEA,	 2011;	
Eurostat,	 2011).	 Furthermore,	 in	 2008	 the	 residential	 sector	 accounted	 for	 27	 percent	 of	 the	 end-use	
greenhouse	 gas	 emissions	 from	 energy	 use	 in	 the	 EU-27	 and	 in	 the	 case	 of	 Portugal,	 16	 percent,	 (EEA,	
2011).	 In	 residential	 buildings	 most	 of	 the	 energy	 used	 is	 required	 for	 domestic	 hot	 water	 and	 space	
heating,	ventilation,	lighting	and	cooling,	with	home	appliances	accounting	for	approximately	one-third	of	
electricity	used,	(European	Commission,	2010).	Space	heating	is	still	the	most	energy	intensive	end-use	in	
																																																																				
1
	OECD	=	Organisation	for	Economic	Co-operation	and	Development	
2	
Total	energy	consumption	and	final	energy	consumption	as	defined	in,	(European	Environment	Agency	[EEA],	2004,	2011;	Official	
Statistics	of	Finland	[OSF],	2013).
2. Energy	use	and	sustainability	
	
16	
EU	homes	and	accounts	for	around	70	percent	of	the	total	final	energy	use,	though	it	has	been	decreasing	
in	comparison	to	other	sources	in	recent	times,	(Backhaus	et	al.,	2012;	BPIE,	2011).	Energy	consumption	for	
water	 heating,	 for	 example,	 remained	 unchanged,	 whereas	 consumption	 for	 electrical	 appliances	 and	
lighting	increased,	(Backhaus	et	al.,	2012;	BPIE,	2011).	Overall,	energy	consumption	in	the	household	sector	
continued	 to	 rise	 annually,	 though	 with	 a	 slower	 growth	 rate	 during	 the	 last	 few	 years,	 (European	
Environment	Agency	[EEA],	2008;	Odyssee	&	MURE,	2011),	which	suggests	that	households	have	become,	
on	average,	more	energy	efficient,	either	deliberately	or	due	to	the	economic	downturn.	
From	a	geographical	perspective	a	difference	appears	to	exist	between	northern	and	southern	European	
countries,	with	heating	needs	in	southern	countries,	such	as	Portugal,	being	lower	due	to	milder	winters,	
(Healy,	2004;	WHO,	2012).	Southern	countries	however	have	a	high	‘relative’	energy	consumption	rate	for	
two	 identified	 reasons:	 firstly	 the	 lack	 of	 sufficient	 thermal	 envelope	 insulation
3
	 in	 southern	 European	
building	stock,	and	secondly	the	fact	that	cooling	becomes	an	important	contributor	to	overall	consumption	
where	homes	are,	in	many	cases,	equipped	with	air	conditioning	systems,	(BPIE,	2011).		
For	 Portugal	 the	 residential	 sector	 similarly	 shows	 rising	 energy	 demands,	 which	 increased	 from	 2.510	
kWh/household	in	2008,	to	2.630	kWh/household	in	2009	and	to	2.671	kW	in	2010,	(DGEG,	2010).	A	more	
in-depth	analysis	of	the	latest	data,	(INE,	2011;	INE	I.P./DGEG,	2011)
4
,	on	household	energy	consumption	in	
Portugal	and	as	depicted	within	Figure	2-1,	shows	that	electricity	emerged	as	the	main	source	of	energy	
consumed	 in	 households,	 excluding	 fuels	 used	 in	 vehicles,	 representing	 42.6	 percent	 of	 total	 energy	
consumption.	 Electricity	 was	 mainly	 consumed	 in	 kitchen	 and	 electrical	 appliances,	 amounting	 to	 41	
percent	and	33	percent	of	the	overall	electricity	consumption	respectively.		
																																																																				
3
	Insulation	of	roof,	exterior	walls	and	floor.	
4
	Data	report	over	the	reference	period	from	October	2009	to	September	2010	unless	otherwise	stated.
2. Energy	use	and	sustainability	
	
17	
	
Figure	2-1:	Distribution	of	energy	consumption	in	households	by	source	type	in	2010,	(INE,	2011;	INE	I.P./DGEG,	
2011).	
Electricity	consumption	has	seen	the	highest	increase	from	15.8	percent	in	1989,	to	27.5	percent	in	1996	
and	now	towards	42.6	percent,	with	electricity	now	being	present	in	99.9	percent	of	the	households.	At	a	
European	level,	(European	Commission,	2010),	there	has	been	an	increase	in	the	overall	available	income	
and	therefore	thermal	comfort,	as	well	as	a	growing	number	of	electrical	appliances	within	households	that	
will	 have	 contributed	 to	 an	 overall	 increase	 in	 energy	 consumption,	 (DGGE/IP-3E,	 2004;	 INE,	 2011;	 INE	
I.P./DGEG,	2011).	Firewood	is	used	in	40	percent	of	households	and	emerged	as	the	second	main	source	of	
energy	consumed	in	Portuguese	households,	with	a	weight	of	24.2	percent	in	the	total	energy	consumed	by	
the	domestic	sector.	This	energy	source	has	been	losing	importance	in	the	past	few	years,	decreasing	from	
60.3	percent	in	1989,	to	41.9	percent	in	1996	and	is	mainly	used	for	house	heating	and	in	the	kitchen,	(INE,	
2011;	 INE	 I.P./DGEG,	 2011).	 This	 predominance	 of	 firewood	 and	 electricity	 as	 the	 main	 energy	 sources	
might	be	related	to	the	recent	introduction	and	consolidation	of	the	gas	network.	Further	to	this,	almost	85	
percent	of	the	energy	within	households	is	being	used	in	three	main	categories	as	mapped	in	Figure	2-2:	
kitchen,	 (39	 percent),	 water	 heating,	 (23.5	 percent)	 and	 house	 heating,	 (21.5	 percent)
5
,	 (INE,	 2011;	 INE	
I.P./DGEG,	2011).	House	heating	thus	has	a	lower	share	of	total	energy	consumption	compared	to	European	
values	that	shows	70	percent	on	an	average,	(Backhaus	et	al.,	2012;	BPIE,	2011).	
																																																																				
5
	Within	the	kitchen,	energy	would	be	spent	on	preparing	food	and	refrigeration,	but	also	on	activities	such	as	laundry	or	dishwashing,	
with	a	predominance	of	energy	intensive	home	appliances.	Water	heating	is	mainly	for	showering	and	accounts	for	almost	¼	of	the	
energy	being	consumed	at	the	household,	(INE	I.P./DGEG,	2011).	
42,6%
24,2%
13,6%
3,0%
9,0%
2,4%
4,3%
0,7% 0,2%
Distribution	of	energy	by	source	type
Electricity
Firewood
LPG	botlles	(butane)
LPG	botlles	(propane)
Natural	Gas
Piped	LPG
Heating	oil
Solar	thermal
Coal
2. Energy	use	and	sustainability	
	
18	
	
Figure	2-2:	Distribution	of	energy	consumption	in	households	by	use	type	in	2010,	(INE	I.P./DGEG,	2011).	
Average	 energy	 usage	 per	 Portuguese	 household	 is	 increasing	 and	 is	 perhaps	 a	 result	 of	 an	 increase	 in	
average	income,	which	is	known	to	influence	the	amount	of	perceived	individual	needs,	(WWF,	2012).	As	
can	 be	 seen	 from	 the	 data	 presented	 in	 this	 section,	 households	 hold	 a	 significant	 potential	 for	 cost	
effective	 savings	 that	 could	 be	 realized	 through	 structural	 and	 policy	 measures.	 Improving	 building	
requirements	or	retrofitting	opportunities	thus	hold	a	great	potential	for	reducing	energy	consumption.	
2.1.1 	Invisibility	of	energy	use	
One	distinct	characteristic	of	energy	consumption	and	in	comparison	to	the	consumption	of	physical	goods,	
is	its	“Invisibility”,	(Darby,	2006),	or	“Doubly	invisibility”,	(Burgess	&	Nye,	2008).	Energy	is	not	used	directly	
at	 home,	 but	 is	 rather	 mediated	 by	 the	 appliances	 people	 have	 and	 practices	 people	 do	 at	 home.	 For	
example,	people	do	not	simply	consume	gas	or	electricity,	but	rather	the	services	these	energy	sources	
provide,	such	as	cooking,	lighting,	or	washing,	(Martiskainen,	2007).	As	such,	energy	might	be	an	abstract	
concept	 and	 it	 might	 be	 difficult	 to	 account	 for	 its	 use,	 or,	 environmental	 impact.	 This	 distinctive	
characteristic	might	therefore	pose	an	additional	barrier	towards	promoting	more	energy	efficient	lifestyles	
and	poses	the	question	as	to	whether	improving	energy	visibility	could	be	a	way	to	reduce	energy	use.	
Research	suggests	this	might	be	the	case,	or	at	least	partially	so.	For	the	case	of	using	information	and	
feedback	provisioning,	as	a	means	to	make	energy	use	visible,	studies	found	that	this	had	resulted	in	less	
energy	use	at	home,	though	it	appeared	to	be	not	enough	to	promote	long-term	change,	nor	were	the	
realized	 savings	 seen	 as	 being	 significant	 with	 regards	 to	 achieving	 sustainable	 energy	 use	 levels,	
(Abrahamse	et	al.,	2005;	Geller,	2002;	Martiskainen,	2007;	Staats,	Wit,	&	Midden,	1996).	As	shown	from	the	
21,5%
0,5%
23,5%
39,1%
10,9%
4,5%
Distribution	of	energy	by	use	type
House	heating
House	cooling
Water	heating
Kitchen
Small	domestic	appliances,	entertainment	
and	computer	equipment
Lighting
2. Energy	use	and	sustainability	
	
19	
literature,	energy	can	become	visible	at	certain	circumstances,	for	instance,	through	energy	bills,	(Brandon	
&	Lewis,	1999;	Darby,	2006),	through	the	services	and	amenities	that	energy	provides,	(Goldblatt,	2005;	
Martiskainen,	2007),	or	when	purchasing	a	new	home	appliance,	(Gardner	&	Stern,	2002,	2008;	Jackson,	
2005).	This	poses	the	question	as	to	whether	energy	becoming	more	visible	could	be	a	way	to	encourage	
the	adoption	of	more	energy	efficient	behaviours.	
2.1.2 	Energy	use	and	energy	saving	at	home	
It	is	a	truism	that	buildings	do	not	use	energy,	but	people	do,	even	though	people	do	not	actually	explicitly	
want	to	use	energy;	it	is	services	like	light	and	comfort	they	really	seek,	(Janda,	2011).	Currently	the	focus	
on	 intervention	 requires	 not	 only	 the	 use	 of	 less	 energy,	 (‘negawatts’),	 but	 also	 more	 efficient	 use.	 An	
example	of	the	former	could	be	to	switch	lights	off	when	leaving	a	room	and	the	latter	could	be	to	change	
to	more	energy	efficient	light	bulbs	in	order	to	provide	lighting	in	a	more	efficient	way.	
Energy	saving	behaviours	can	be	distinguished	between	efficiency	and	curtailment	behaviours.	Efficiency	
behaviours	are	infrequent,	one-off	type	of	behaviours,	which	often	entail	an	investment,	such	as	loft	or	
cavity	 wall	 insulation,	 or	 buying	 an	 energy	 efficient	 air	 conditioner,	 (Abrahamse	 et	 al.,	 2005;	 Gardner	 &	
Stern,	2002;	Kempton	et	al.,	1992).	Curtailment	behaviours	in	contrary	are	those	that	must	be	performed	
frequently,	involving	repetitive	efforts	to	reduce	energy	and	involve	more	operational	day	to	day	habits	and	
routines,	such	as	lowering	the	thermostat	and	turning	lights	and	appliances	off,	(Abrahamse	et	al.,	2005;	
Gardner	 &	 Stern,	 2002;	 Kempton	 et	 al.,	 1992).	 Each	 of	 these	 two	 groups	 requires	 different	 levels	 of	
investment	in	time,	money	or	individual	effort	and	commitment	to	perform.	For	example,	to	insulate	one’s	
loft	requires	the	time	to	look	for	an	adequate	supplier,	to	hire	someone	to	perform	the	work	and	demands	
a	certain	amount	of	investment;	but	it	would	be	a	one-off	action.	On	the	other	hand,	to	maintain	a	lower	
thermostat	 setting,	 (even	 if	 one	 has	 a	 properly	 insulated	 loft),	 requires	 a	 certain	 level	 of	 knowledge,	
willingness	and	commitment	not	to	increase	room	temperature	on	a	day-to-day	basis;	this	is	not	a	one-off	
action,	but	a	frequently	performed	one,	a	so-called	routine	behaviour.	
Less	unanimous	agreement,	than	on	the	grouping	of	these	two	behaviours,	can	be	found	in	the	impact	they	
can	 have	 in	 terms	 of	 energy	 saving	 and	 conservation,	 and	 there	 is	 some	 disagreement	 as	 to	 whether	
curtailment	 or	 efficiency	 behaviours	 are	 more	 effective	 in	 reducing	 energy	 use	 at	 home,	 (Martiskainen,
2. Energy	use	and	sustainability	
	
20	
2007).	Some	studies	suggest	that	curtailment	behaviours	could	initiate	sustainable,	long-term	behavioural	
changes,	 (Geller,	 2002),	 while	 others	 suggest	 that	 efficiency	 behaviours	 are	 generally	 more	 effective	 in	
obtaining	 actual	 energy	 savings,	 (Abrahamse	 et	 al.,	 2005;	 Gardner	 &	 Stern,	 2008).	 In	 addition	 to	 this,	
curtailment	 behaviours	 might	 be	 perceived,	 by	 individuals,	 as	 negligible	 behaviours	 when	 it	 comes	 to	
energy	savings,	as	individually	they	would	generate	only	small	savings	and	therefore,	in	order	to	produce	an	
impact	would	require	adoption	by	many	people,	(Winter	&	Koger,	2004,)	and/or	the	adoption	of	a	number	
of	behaviours	by	each	individual.	
2.2 	Determinants	of	energy	use	at	home	
The	 way	 people	 use	 energy	 in	 the	 home	 is	 the	 result	 of	 a	 mixture	 of	 socio-economical-techno-cultural	
factors	that	frames	needs,	opportunities,	belief	systems	and	abilities,	as	illustrated	in	Figure	2-3.	
	
Figure	2-3:	Main	factors	influencing	consumer	behaviour	and	emergence	of	consumption	practices,	(EEA,	2013).	
Energy	use	at	home	is	often	explained	as	based	on	a	set	of	enabling	variables	and	existing	conditions.	For	
instance,	 the	 European	 Environment	 Agency,	 (EEA,	 2013),	 suggested	 a	 number	 of	 factors	 influencing	
consumer	behaviours	and	emerging	practices	that	could	support	the	understanding	of	energy	use	at	home,	
as	well	as	the	adoption	of	more	energy	efficient	behaviours.	This	section	will	discuss	determinants	that	had	
been	 identified	 from	 the	 literature	 as	 influencing	 energy	 use	 at	 home,	 namely,	 social	 and	 cultural	
influences,	comfort,	convenience	and	needs,	norms;	technological	developments;	as	well	as	economic	and	
demographic	 trends,	 (Abrahamse	 et	 al.,	 2005;	 BPIE,	 2011;	 DGGE/IP-3E,	 2004;	 Goldblatt,	 2005;	 INE	
I.P./DGEG,	2011;	Lomas,	2010;	Spaargaren	&	van	Vliet,	2000;	Wilhite	&	Lutzenhiser,	1999)	and	that	can	be	
of	 an	 internal,	 external,	 social,	 or	 structural	 nature,	 (Abrahamse	 et	 al.,	 2005;	 Gardner	 &	 Stern,	 2002;
2. Energy	use	and	sustainability	
	
21	
Kempton,	Reynolds,	Fels,	&	Hull,	1992;	Martiskainen,	2007;	Nye	et	al.,	2010;	Prendergrast	et	al.,	2008).	The	
work	of	Jackson	(2005)	shows	for	example	that	internal	determinants	might	consist	of	attitudes,	beliefs	and	
norms,	while	external	determinants	could	constitute	regulations.	Abrahamse	et	al.	(2005)	in	contrast	shows	
that	determinants	might	include	wider	societal,	as	well	as	personal	factors,	while	the	work	of	Dholakia	and	
Dholakia	(1983)	shows	that	determinants	could	result	from	a	series	of	nested	and	interlocking	choices,	in	
which	 macro-choices	 delimit	 and	 define	 the	 scope	 of	 micro-choices	 and	 where	 household	 energy	 use	 is	
seen	to	be	as	not	only	the	result	of	a	choice	among	behavioural	alternatives	but	where	the	production	of	
such	alternatives	is	also	viewed	as	the	result	of	a	social	choice	process.	Thus	there	appears	to	be	a	diversity	
of	macro-	and	micro-	factors.	Macro-level	factors	such	as	technological	development,	economic	growth,	
demographic	factors,	institutional	factors	and	cultural	development	appear	to	influence	behaviour	at	the	
broader	 level,	 while	 micro-level	 factors	 such	 as	 motivation,	 opportunity	 and	 ability	 appear	 to	 shape	
behaviour	at	the	individual	level,	(Darnton,	2008;	Jackson,	2005;	Nye	et	al.,	2010;	Prendergrast	et	al.,	2008;	
Stern,	2000).	Thus	energy	use	is	determined	by	multiple	conscious	and	unconscious	processes,	driven	by	
internal	psychological	variables,	such	as	norms,	beliefs	or	values,	as	well	as	external	variables,	(e.g.	social,	
economic	physical),	drivers	and	constraints,	personal	capabilities,	or	habits	and	routines,	(Jackson,	2005;	
Nye	 et	 al.,	 2010;	 Stern,	 2000).	 As	 such	 energy	 consumption	 is	 not	 a	 behaviour	 in	 itself,	 but	 rather	 a	
consequence	 of	 particular	 behaviours,	 (Becker,	 Seligman,	 Fazio,	 &	 Darley,	 1981).	 Consequently	 to	
understand	 and	 influence	 behaviours	 on	 energy	 use	 would	 require,	 firstly,	 an	 understanding	 of	 the	
determinants	of	energy	use	behaviours.	
2.2.1 	Social	and	cultural	influences		
Social	and	cultural	factors,	such	as	thermal	comfort,	cleanliness	and	convenience	in	the	home,	or	ambient	
lighting	that	impact	the	amount	of	energy	used	at	home	are	influenced	both	by	individual	preferences	and	
common	social	understandings,	(Giddens,	1984;	Lewis,	1969).	As	an	example,	for	Portugal	the	penetration	
rate	 of	 refrigerators,	 washing	 machines	 and	 televisions	 at	 home	 has	 increased	 to	 close	 to	 100	 percent,	
suggesting	that	owning	these	appliances	is	now	considered	to	be	a	standard,	(INE,	2012).	This	introduction	
of	home	appliances	brings	along	social	practices	that	evolve	over	time	and	develop	into	social	norms	that	
establish	standards	that	can	lock	individuals	into	what	is	considered	to	be	a	‘normal’	practice.	This	can	lead	
to	individuals	finding	it	hard	to	change	their	domestic	routines	and	behaviours,	or	to	change	them	in	a	way
2. Energy	use	and	sustainability	
	
22	
that	would	bring	about	a	significant	impact	in	terms	of	energy	use,	(Goldblatt,	2005;	Maréchal,	2010;	Shove,	
2004).	This	understanding	of	behaviour	as	an	outcome	of	routinized,	socially	learned	habits	or	practices,	
embedded	 into	 particular	 socio-technical	 infrastructures,	 or	 a	 system	 of	 provision,	 can	 be	 traced	 to	
sociology	and	to	the	on-going	debate	about	structure	vs.	agency;	which	defines	the	relationships	between	
individuals,	communities	and	society	in	more	detail.	If	on	the	one	hand,	human	behaviour	is	constrained	by	
structural	factors,	on	the	other,	social	structure	is	a	human	product	of	itself.	This	is	to	say	that	established	
rules	 and	 ways	 of	 doing	 things	 can	 be	 changed	 once	 people	 start	 to	 ignore	 them,	 replace	 them,	 or	
reproduce	 them	 differently	 and	 as	 a	 result	 develop	 a	 new	 social	 practice,	 (Giddens,	 1984).	 There	 are,	
however,	limits	as	to	how	much	individuals	can	change	social	structure,	(Heiskanen	et	al.,	2009).	This	relates	
to	the	debate	around	whether	consumers	are	free	to	make	choices	about	their	own	actions,	or	whether	
forces	outside	their	control	impose	those,	(Giddens,	1984).	Giddens’	work	(1984),	for	example	has	been	
setting	the	ground	for	viewing	consumption	as	a	set	of	social	practices	that	are	influenced	on	the	one	hand	
by	 social	 norms	 and	 lifestyle	 choices,	 and	 on	 the	 other,	 by	 the	 institutions	 and	 structures	 of	 society,	 as	
exemplified	in	Figure	2-4,	(Giddens,	1984;	Randles,	2009;	Spaargaren	and	van	Vliet,	2000).	
	
Figure	2-4:	An	Actor-Structure	Model	of	Consumption,	(adapted	from	Spaargaren	and	van	Vliet	(2000)).	
The	 model	 in	 Figure	 2-4	 shows	 the	 interplay	 of	 social	 norms,	 lifestyle	 choices	 and	 the	 institutions	 and	
structures	of	society,	which	comprise	the	two	basic	pillars	of	sociological	theory.	The	model	suggests	that
2. Energy	use	and	sustainability	
	
23	
shifting	consumption	patterns	requires	‘raising’	routine	behaviours	from	a	level	of	practical	consciousness
6
	
to	discursive	consciousness
7
,	therefore	making	them	more	visible.	This	distinction	can	be	of	relevance	since	
most	 of	 the	 everyday,	 routine	 actions	 that	 consume	 energy	 at	 home	 are	 performed	 in	 practical	
consciousness,	 (Spaargaren	 &	 van	 Vliet,	 2000),	 reminiscent	 of	 being	 under	 automatic	 pilot	 control	 that	
appears	to	lock-in	individuals.	
2.2.2 	Comfort,	convenience	and	needs	
In	 today’s	 developed	 economies	socially	 perceived	 needs	 frequently	 relate	 to	 comfort,	 convenience	 and	
wellbeing,	and	are	perceived	as	being	part	of	a	‘normal’	lifestyle	which	needs	to	be	satisfied,	(Lehman	&	
Geller,	 2004;	 WWF,	 2012).	 Comfort	 and	 convenience	 needs	 are	 the	 result	 of	 technological	 progress,	
increased	income	levels,	availability	of	labour	saving	appliances	and	cultural/social	dynamics,	creating	new	
practices	 that	 embed	 into	 the	 social	 fabrics	 of	 daily	 lives,	 (Shove,	 2009).	 Examples	 of	 this	 are	 the	
automation	of	jobs	previously	done	by	hand,	and	substituting	energy-using	appliances	like	computers	and	
consoles	where	in	the	past	people	would	have	worked	using	pen	and	paper,	or	entertained	themselves	with	
board	games	or	books.	Comfort	conditions,	in	general,	are	socially	influenced	and	may	change	with	time	as	
design,	 activity,	 and	 technology	 change,	 (Shove	 2003).	 The	 gap	 between	 estimated	 and	 actual	 energy	
performance	in	housing	tends	to	directly	increase	to	increasing	comfort	levels	beyond	what	was	predicted,	
(Stevensen	and	Rijal,	2010).	One	such	examples	can	be	seen	in	the	increasing	penetration	of	central	heating	
and	cooling	systems	of	the	last	few	years	that	seems	to	be	accompanied	by	a	growing,	perceived	need	of	
improving	indoor	thermal	comfort,	(Eurostat,	2007).				
2.2.3 	Norms	and	energy	efficiency		
Norms	 are	 rules	 and	 standards	 that	 impact	 energy	 use	 as	 they	 guide	 and/or	 constrain	 social	 behaviour,	
(Cialdini	&	Trost,	1998).	Within	the	literature	a	number	of	different	norms	are	defined,	such	as	personal	and	
moral	 norms,	 (Schwartz,	 1970,	 1977),	 subjective	 norms,	 (Ajzen	 &	 Fishbein,	 1980)	 and	 descriptive	 and	
																																																																				
6
	Practical	consciousness	consists	of	all	things	which	actors	know	tacitly	about	how	to	‘go	on’	in	the	contexts	of	social	life	without	being	
able	to	give	them	discursive	expression	(…)	describing	behaviours	that	reside	in	the	‘non-consciousness	(Giddens,	1984).	
7
	Discursive	consciousness	can	manifest	in	purposeful	and	intentional	behaviour,	(Giddens,	1984).
2. Energy	use	and	sustainability	
	
24	
injunctive	norms,	(Cialdini	et	al.,	1991;	Cialdini	et	al.,	1990).	Norms	might	emerge	from	interaction	with	
others,	 they	 may	 or	 may	 not	 be	 stated	 explicitly	 and	 sanctions	 for	 deviating	 from	 norms	 are,	 mostly,	
imposed	by	social	networks,	not	the	legal	system,	(Cialdini	&	Trost,	1998).	Norms	further	tend	to	motivate	
and	 constrain	 individual	 actions	 by	 promising	 social	 rewards	 and	 sanctions	 for	 acting,	 or	 not	 acting,	 in	
certain	kinds	of	ways.	For	instance,	one	might	not	litter	not	only	because	one	might	get	a	fine,	but	also	
because	 one	 does	 not	 want	 others	 to	 think,	 “I’m	 the	 kind	 of	 person	 that	 litters”.	 Individuals	 tend	 to	
negotiate	and	inform	much	of	their	behaviour	on	the	basis	of	what	others	do	around	them	and	by	simply	
copying	 the	 way	 others	 around	 them	 behave.	 This	 is	 used	 as	 a	 means	 to	 bypassing	 the	 mental	 effort	
involved	in	thinking	it	out	for	oneself	and/or	to	free	up	cognitive	resources	for	more,	perceived,	important	
tasks,	(Cialdini	et	al.,	1990).	Whether	and	how	one	responds	to	a	norm	also	depends	on	which	kind	of	norm	
is	salient	for	that	specific	circumstance,	(Cialdini,	1993;	Cialdini	et	al.,	1991;	Cialdini	et	al.,	1990;	Steg,	2003).	
Within	this	structure,	norms	influence	behaviour	through	imitation,	social	comparison,	or	social	learning	
theory,	(Bandura,	1977b,	1986;	Cialdini	et	al.,	1991).	
For	the	theoretical	relation	between	norms	and	environmental	significant	behaviours
8
,	an	ample	body	of	
available	 literature	 exists,	 (Abrahamse	 et	 al.,	 2005;	 de	 Groot,	 Steg,	 &	 Dicke,	 2007;	 Guagnano,	 2001;	
Osterhus,	 1997;	 Schultz	 et	 al.,	 2005),	 but	 less	 evidence	 can	 be	 found	 within	 the	 literature	 for	 the	
contribution	 of	 norms	 to	 encourage	 the	 adoption	 of	 more	 energy	 efficient	 behaviours.	 Currently,	 the	
socially	accepted	norm	appears	to	be	towards	the	acceptance	of	an	over-consumption	of	energy	and	thus	
adopting	more	energy	efficient	behaviours	will	be	difficult	to	achieve	without	such	behaviours	being	viewed	
as	the	social	norm,	(Schwartz,	1977;	Stern,	1999,	2000).	In	addition	to	this,	the	growing	number	of	needs	as	
well	as	owned	home	appliances	might	be	seen	as	an	indicator	of	the	social	norm	moving	towards	a	higher	
level	of	consumption,	(Cialdini	et	al.,	1990,	1991;	Triandis,	1977).	Norms	further	appear	to	impact	behaviour	
differently.	 This	 is	 to	 say	 that	 personal	 norms	 and	 attitudes	 that	 are	 based	 on	 altruistic	 and	
biospheric/ecological	values	seem	to	be	more	effective	at	leading	to	simple,	repetitive,	low-cost,	(effort,	
money,	and	time),	energy	saving	behaviours,	(Black,	Stern,	&	Elworth,	1985;	Heberlein	&	Warriner,	1983;	
																																																																				
8
	Environmentally	significant	behaviour	is	behaviour	that	does	not	“threaten	human	health,	welfare,	or	other	things	people	value”,	
(Stern,	1997,	p.	15)	and	that	is	characterized	by	its	“positive	impact	on	the	availability	of	materials	or	energy	from	the	environment	
and/or	by	the	extent	to	which	the	behaviours	positively	alter	the	structure	and	dynamics	of	ecosystems	or	the	biosphere”,	(Stern,	
2000,	p.	408).
2. Energy	use	and	sustainability	
	
25	
Stern,	1992).	Specifically,	research	indicates	that	altruistic/social	norms	are	much	more	strongly	related	to,	
“low	 constraint”,	 environmentally	 friendly	 behaviours,	 such	 as	 adjusting	 a	 thermostat,	 than	 they	 are	 to,	
“high	constraint”,	behaviours,	such	as	major	capital	investments	to	improve	the	energy	efficiency	of	one’s	
home,	(Black	et	al.,	1985;	Lindenberg	&	Steg,	2007).	For	example,	an	intention	to	reduce	car	use	may	be	
seen	 as	 a	 more	 costly	 behaviour	 compared	 to	 buying	 organic	 food	 because	 of	 the,	 perceived,	 higher	
inconvenience	associated	with	reducing	car	use,	(Abrahamse	et	al.,	2005;	Poortinga	et	al.,	2004).	
2.2.4 	Economic	influences	
Economics	and	its,	“Rational	man”,	principle,	(Mill,	1836),	suggest	that	people	are	driven	by	self-economic	
interest,	i.e.	people	will	maximize	their	set	of	preferences	and	their	utility,	(i.e.	the	value	attached	to	an	
outcome).	In	a	period	of	rising	energy	prices,	(Odyssee	&	MURE,	2011)	and	in	accordance	to	the,	“Rational	
man”,	approach,	reducing	energy	bills	should	thus	be	a	primary	motivation	for	saving	energy.	This	is	to	say,	
one	would	expect	energy	use	to	fall	once	prices	go	up,	in	order	to	not	increase	the	percentage	of	income	
dedicated	to	energy.	However,	evidence	suggests	that	the	relation	between	price	and	energy	use	is	not	1	to	
1,	meaning,	for	instance,	a	10	percent	increase	in	price	does	not	lead	to	a	10	percent	decrease	in	energy	
use.	This	phenomenon	is	known	within	the	economics	literature	as,	‘price	elasticity’,	i.e.	the	percentage	
change	in	one	variable	following	a	percentage	change	in	another,	holding	other	variables	constant,	(Sorrell,	
2007).	Demand	for	energy	is	often	perceived	to	be,	‘inelastic’,	in	the	short	term,	i.e.	energy	use	does	not	
change	straight	away	when	prices	increase.	But,	it	is	seen	to	be,	‘elastic’,	in	the	long	term,	i.e.	a	few	years	
after	price	increases	households	are	able	to	modify	to	save	energy.	This	is	to	say	that	in	the	short	term,	
rising	prices	might	not	be	effective	in	significantly	stimulating	demand	reduction.	This	is	in	the	uptake	of	
demand	reduction	measures	that	could	save	energy	at	home,	(Department	of	Energy	&	Climate	Change	
[DECC],	2011).	An	analysis	of	US	demand	elasticity	in	response	to	price	rises	suggests	that	a	ten	per	cent	
increase	in	electricity	prices	only	decreases	demand	by	around	one	per	cent,	(Nakajima	&	Hamori,	2010).	
Elasticity	 might	 be	 one	 of	 the	 reasons	 why	 higher	 energy	 prices,	 government	 taxes	 and	 subsidies	 have	
apparently	not	had	the	expected	impact	in	reducing	energy	consumption	at	a	household	level,	(Spaargaren	
&	van	Vliet;	2000).
2. Energy	use	and	sustainability	
	
26	
2.2.5 	Income	levels	and	energy	poverty	
In	the	case	of	income	levels,	the	literature	provides	some	apparent	contradictory	findings.	Evidence	has	
equally	 shown	 that	 higher	 income	 levels	 often	 relate	 to	 higher	 energy	 use,	 (DECC,	 2011),	 as	 well	 as	 for	
apparent	dissociation,	with	similar	income	level	households	using	significantly	different	levels	of	energy,	
(Gatersleben	et	al.,	2002).	If	indeed	energy	use	increases	with	income	level,	then	one	could	expect	more	
affluent	households	to	use	more	energy	than	less	affluent	ones.	However,	poorer	households	are	also	more	
likely	to	live	in	poorly-insulated	homes	and	less	likely	to	be	able	to	improve	their	homes’	energy	efficiency,	
(Scottish	Government,	2010).	For	instance,	for	those	in	fuel	poverty,	they	might	not	be	able	to	afford	to	
spend	more	on	energy	and	are	forced	into	using	less	energy	if	prices	rise.	Conversely,	wealthier	households	
may	 be	 more	 prone	 to	 ignoring	 ‘avoidable’	 energy	 use,	 such	 as	 heating	 unused	 rooms,	 or	 leaving	
unnecessary	lights	on.	With	this	the	demand	for	energy	tends	to	be	more	elastic	in	poorer	households	than	
in	 wealthier	 ones,	 meaning	 that	 they	 tend	 to	 use	 less	 energy	 if	 prices	 rise.	 Further	 to	 this,	 poorer	
households	 might	 also	 experience	 energy	 poverty,	 which	 is	 a	 situation	 where	 a	 household	 is	 unable	 to	
access	a	socially-	and	materially-necessitated	level	of	energy	service	in	the	home,	(Buzar,	2007a).	According	
to	 Boardman	 (1991,	 2010),	 a	 household	 is	 said	 to	 be	 in	 fuel	 poverty	 if	 it	 needs	 to	 spend	 more	 than	 10	
percent	of	its	(disposable),	income	on	household	fuel,	(energy),	including	heating	the	house	to	acceptable	
World	Health	Organization	levels
9
.	According	to	the	literature,	fuel	poverty	results	from	a	combination	of	
low	income,	low	energy	performance	dwellings	and	increasing	energy	prices,	(UK	Government,	2013)	and	
there	 is	 equally	 evidence	 that	 southern	 Europe	 suffers	 from	 the	 highest	 levels	 of	 fuel	 poverty	 and	 the	
poorest	housing	conditions	within	the	EU,	(Healy,	2003;	SEI,	2003).	The	inability	to	afford	to	heat	the	home	
adequately	is	particularly	pronounced	across	eastern	and	southern	European	states,	with	over	30	per	cent	
of	 households	 in	 Portugal,	 Bulgaria	 and	 Cyprus	 declaring	 this	 inability,	 (The	 University	 of	 York,	 n.d.).	
Magalhães	and	Leal	(2012)	estimate	a	92	percent	fuel	poverty	rate	for	mainland	Portugal	under	nominal	
conditions	 by	 considering	 a	 tariff	 of	 0.089€	 per	 kWh	 of	 energy	 supplied.	 Healy	 (2004)	 reported	 that	 in	
Portugal	only	6	percent	had	cavity	wall	insulation,	3	percent	double-glazing,	2	percent	floor	insulation	and	6	
percent	roof	insulation	in	their	homes,	(one	of	the	usual	pre-conditions	for	fuel	poverty).	In	addition	to	this,	
																																																																				
9
	 The	 World	 Health	 Organisation	 takes	 21ºC	 as	 a	 benchmark	 temperature	 for	 those	 more	 vulnerable,	 such	 as	 the	 elderly	 and	
handicapped	and	a	minimum	temperature	of	16ºC	for	able-bodied,	healthy	people,	but	recommends	a	minimum	of	18ºC	for	sedentary	
activities.
2. Energy	use	and	sustainability	
	
27	
nearly	 a	 quarter	 of	 Portuguese	 households	 stated	 that	 they	 had	 rotten	 window	 frames,	 while	 a	 third	
revealed	 that	 they	 had	 patches	 of	 condensation	 on	 indoor	 walls,	 two	 good	 indicators	 of	 poor	 energy	
efficiency,	(Healy,	2004).	Further	to	this,	19	percent	of	households	in	Portugal	were	suffering	from	leaking	
roofs,	indicating	the	absence	of	adequate	roof	insulation,	(Healy,	2004)	and	the	latest	data	for	Portugal	
reveals	that	26.8	percent	reported	their	inability	to	keep	their	home	adequately	warm,	(Eurostat,	2013).	An	
additional	problem	in	Mediterranean	states	is	the	need	for	cooling,	with	30	percent	of	the	population	in	the	
8	states	bordering	the	Mediterranean	Sea	reporting	that	they	are	unable	to	keep	their	homes	adequately	
cool	in	summer,	(SILC,	2007).	Even	though	heating	seems	still	to	be	the	main	issue	in	the	short	term,	cooling	
is	likely	to	become	an	increasingly	important	issue	over	the	coming	years,	in	particular	with	rising	global	
temperatures,	 (ECI,	 2005).	 The	 limited	 extent	 of	 certain	 types	 of	 networked	 energy	 infrastructures,	
(particularly	 gas),	 means	 that	 in	 addition	 to	 inefficient	 residential	 stocks	 and	 affordability	 issues,	 energy	
deprivation	is	also	predicated	upon	the	spatial	and	technical	limitations	associated	with	switching	towards	
more	affordable	fuel	sources	in	the	home,	(Buzar,	2007a,	2007b,	2007c).	
Besides	decreasing	the	quality	of	life	and	influencing	social	fulfilment,	there	is	also	a	strong	associations	
between	 inadequately	 heated	 homes	 and	 increased	 rates	 of	 morbidity	 and	 mortality,	 (Harrington	 et	 al.,	
2005).	The	fact	that	in	Portugal,	the	excess	of	winter	mortality	rates	and	hospital	episodes	compared	to	that	
of	summer	is	among	the	highest	in	Europe,	adds	to	the	suspicion	that	households	are	not	heating	their	
homes	 adequately	 and	 to	 an	 association	 with	 mortality	 rates	 and	 hospital	 episodes,	 (Eurowinter	 Group,	
1997;	 Gascoigne,	 Morgan,	 Gross,	 &	 Goodwin,	 2010;	 Healy,	 2004;	 IPCC,	 2007;	 McMichael,	 Woodruff,	 &	
Hales,	2006).		
2.2.6 	Demographic	trends	
In	addition	to	economic	influences,	there	are	two	demographic	trends	that	have	been	observed	over	the	
last	 few	 decades	 that	 seem	 to	 influence	 energy	 use:	 household	 size	 and	 composition.	 Today	 people	 in	
industrialised	 countries	 tend	 to	 live	 in	 larger	 houses,	 with	 a	 lower,	 average	 number	 of	 occupants	 per	
household	and	a	growing	number	of	single-occupancy	dwellings,	(Goldblatt,	2005).	A	larger	home	implies	
increased	floor	and	air	space	to	heat,	or	cool	and	thus	an	increase	in	the	required	energy	to	maintain	a	
comfortable	temperature	in	the	house.	Evidence	suggests	that	the	more	people	there	are	in	a	household
2. Energy	use	and	sustainability	
	
28	
the	more	energy	efficient	per	capita	that	household	becomes,	meaning	that	single-person	households	tend	
to	use	more	energy	per	person	when	compared	to	multi-person	households,	(Energy	Saving	Trust,	2012).	As	
a	result	of	this,	projected	population	growth	might	be	less	important	than	the	average	number	of	occupants	
per	household	and	in	particular,	the	number	of	single	occupancy	dwellings.	
2.2.7 	The	role	of	infrastructure	and	technological	factors	in	influencing	energy	use	at	home	
During	 the	 past	 few	 decades	 there	 has	 been	 an	 extraordinary	 growth	 in	 the	 number	 and	 choices	 of	
consumer	 energy-using	 products,	 (Energy	 Saving	 Trust,	 2011).	 This	 is	 in	 particular	 true	 for	 labour	 saving	
devices	and	personal/home	entertainment	systems,	with	the	associated	energy	consumption	contributing	
to	a	continuing	upward	trend	in	domestic	electricity	consumption,	(Energy	Saving	Trust,	2011).	Further	to	
this,	 technologies	 that	 are	 designed	 to	 ‘improve’	 people’s	 lives,	 such	 as	 air-conditioning,	 have	 rapidly	
developed	 from	 being	 a	 luxury	 towards	 becoming	 essentials,	 (Shove,	 2003).	 Despite	 improvements	 in	
energy	efficiency	in	homes	and	products,	the	demand	for	energy	has	outstripped	this	improvement,	(Energy	
Saving	Trust,	2011;	Odyssee	&	MURE,	2011).	This	suggests	that	even	though	technological	developments	
increased	the	energy	efficiency	of	appliances,	part	of	this	efficiency	gain	is	being,	taken	back	(Odyssee	&	
MURE,	2011).	This,	take	back,	could	be	one	explanation	for	the	difference	between,	actual	energy	efficiency	
and	 potential	 efficiency,	 also	 known	 as	 the	 energy	 efficiency	 gap,	 (Feenstra	 et	 al.,	 2009).	 Overall	 four	
reasons	seem	to	contribute	to	‘take	back’.	Firstly,	due	to	the	growing	number	of	energy	using	appliances	to	
be	found	in	the	average	home,	(Energy	Saving	Trust,	2011).	Secondly,	the	way	these	appliances	are	used,	
(Energy	Saving	Trust,	2011;	Goldblatt,	2005;	INE	I.P./DGEG,	2011;	Lomas,	2010).	Thirdly,	within	the	socio-
technical	system	and	the	way	that	individual	choices	are	constrained	and	shaped,	the	so-called	behavioural	
lock-in,	 (Energy	 Saving	 Trust,	 2011;	 Direção	 Geral	 de	 Energia	 e	 Geologia	 [DGEG],	 2010;	 Maréchal,	 2010;	
Quercus,	2008).	The	fourth	reason	relates	to	the,	‘rebound	effect’,	where	energy	efficiency	improvements	
may	impact	on	the	demand	for	other	goods	and	services,	as	the	savings	from	one	appliance	can	be	used	on	
other	energy	using	activities,	(Binswanger,	2001;	Khazzoom,	1980;	Odyssee	&	MURE,	2011;	Sorrell,	2007).	
However	technological	developments	are	not	limited	to	appliances	but	also	to	the	building	characteristics.	
Energy	use	at	home	is	influenced	by	building	characteristics	such	as	age,	orientation,	size,	building	envelope	
(i.e.	roof,	exterior	walls,	and	floor)	and	the	performance	of	installed	heating/cooling	system,	(BPIE,	2011;
2. Energy	use	and	sustainability	
	
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DGGE/IP-3E,	2004;	Goldblatt,	2005).	The	characteristics	of	a	building,	its	design	and	its	technical	standards	
do	not	only	influence	well-being,	but	they	also	define	how	much	energy	is	consumed	in	and	by	a	building,	
and	as	a	consequence,	how	much	heating,	ventilation	and	cooling	energy	is	needed	to	create	a	comfortable	
environment	based	on	respective	climate	conditions,	(BPIE,	2011).	Significant	savings	in	energy	use	could	be	
achieved	by	improving	building	characteristics	and	the	European	Union	has	been	active	in	this	area	and	has	
passed	a	number	of	European	Directives,	(Energy	Performance	of	Buildings	Directive	-	EPBD),	so	as	to	define	
the	 minimum	 standards	 to	 be	 used	 in	 new	 buildings,	 as	 well	 as	 within	 the	 refurbishment	 of	 existing	
buildings.	However,	since	buildings	have	a	long	service	life,	this	may	not	deliver	immediate	energy	savings,	
or	at	least	not	to	the	level	that	might	be	required.	Even	though	‘new’	buildings	are	expected	to	consume	
around	¼	less	than	the	ones	built	in	1990,	they	accounted	for	only	21	percent	of	total	building	stock	in	
Europe,	thus	the	impact	of	more	energy	efficient	ways	of	building	will	take	time	to	produce	global	results,	
(BPIE,	 2011;	 Odyssee	 &	 MURE,	 2011).	 This	 is	 to	 say	 that	 people	 might	 be	 temporally	 locked	 into	 the	
buildings	they	live	in,	(Maréchal,	2010)	and	that	it	will	require	time	to	increase	the	energy	efficiency	of	the	
buildings	and	to	reduce	the	amount	of	energy	being	used.	The	same	long-term	dilemma	can	be	seen	in	the	
heating/cooling	 systems	 of	 buildings	 that	 equally	 have	 a	 relatively	 long	 lifetime,	 which	 in	 the	 case	 of	
standard	boilers	is	normally	15-20	years,	(Energy	Saving	Trust,	2011).	For	this	particular	case	and	due	to	low	
substitution	rates,	effort	might	rather	be	focused	on	the	effective	use	of	heating/cooling	systems,	rather	
than	on	the	substitution,	which	requires	investment,	(Energy	Saving	Trust,	2011).	
2.2.8 	The	rebound	effect	and	its	influence	on	determining	energy	use	at	home	
The	 potential,	 energy	 savings,	 from	 improved	 energy	 efficiency	 are	 commonly	 estimated	 using	 basic	
physical	principles	and	engineering	models.	However,	the	savings	that	are	realized	in	practice	generally	fall	
short	of	these	engineering	estimates.	One	explanation	for	this	is	that	improvements	in	energy	efficiency	
apparently	encourage	a	greater	use	of	the	services,	a	response	known	as	the	energy	efficiency,	rebound	
effect,	 or,	 take-back	 effect,	 (Khazzoom,	 1980).	 Generally	 speaking	 this	 rebound,	 or	 take-back	 effect	 is	
measured	by	the	difference	between	the	projected	and	actual	savings	due	to	increased	efficiency	and	is	
normally	expressed	as	a	percentage	of	the	expected	energy	savings	from	energy	efficiency	improvements;	a	
ratio	of	the	lost	benefit	compared	to	the	expected	environmental	benefit,	once	consumption	is	constant,
2. Energy	use	and	sustainability	
	
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(Grubb,	 1990;	 Sorrell,	 2007).	 Thus	 a	 rebound	 effect	 of	 20	 percent	 means	 that	 only	 80	 percent	 of	 the	
expected	 energy	 savings	 have	 been	 achieved.	 In	 accordance	 to	 Gottron	 (2001)	 and	 Sorrell	 (2007)	 three	
different	types	of	rebound	effect	might	be	observed:	
• Direct	 rebound	 effect:	 energy	 efficiency	 improvements	 make	 energy	 services	 cheaper,	 so	
consumption	of	those	services	increase	once	the	consumer	chooses	to	use	more	of	the	resource	
instead	of	realizing	the	energy	cost	savings;	e.g.	people	have	their	loft	insulated	and	later	raise	
their	thermostat	to	a	higher	temperature.	
• Indirect	 rebound	 effects:	 even	 if	 consumption	 of	 energy	 services	 remains	 unchanged,	 the	
consumer	 can	 chose	 to	 spend	 the	 money	 saved	 by	 buying	 other	 goods,	 which	 use	 the	 same	
resource;	e.g.	individuals	have	their	loft	insulated	or	buy	a	fuel-efficient	car	and	therefore	realize	
savings	on	fuel	bills,	but	then	use	those	savings	to	later	go	on	a	long	haul	vacation.	
• Macroeconomic	effects:	any	reductions	in	energy	demand	will	translate	into	lower	energy	prices	
that	encourage	increased	energy	consumption.	Decreased	demand	for	a	resource	leads	to	a	lower	
resource	price,	making	new	uses	economically	viable;	e.g.	new,	more	energy	efficient	technologies	
that	make	items,	such	as	air	conditioners	more	accessible	and	affordable	to	users.	
Direct	and	indirect	rebound	effects	appear	to	vary	widely	depending	on	technologies,	sectors	and	income	
groups	and	often	they	cannot	be	quantified	with	much	confidence,	(Sorrell,	2007).	This	appears	to	support	
on-going	discussion	and	lack	of	agreement	regarding	size	and	impact	of	the	rebound	effect.	On	the	one	
hand	findings	show	that	rebound	effects	could	completely	offset	the	energy	savings	from	improved	energy	
efficiency,	(Brookes,	2000;	Guertin,	Kumbhakar,	&	Duraiappah,	2003;	Herring,	2006;	Sorrell,	2007).		Recent	
research	 has	 shown	 take-back	 examples	 where	 thermal	 efficiency	 improvements	 were	 out-weighed	 by	
increases	 in	 energy	 levels	 for	 lights	 and	 appliances,	 (Lomas,	 2010;	 Wright,	 2008).	 On	 the	 other	 hand,	
findings	 indicate	 that	 the	 rebound	 effect	 is	 of	 minor	 importance,	 largely	 due	 to	 the	 understanding	 that	
demand	for	those	services	appears	to	be	inelastic	in	most	cases,	as	energy	cost	represent	only	a	small	share	
of	the	total	costs	of	those	services,	(Lovins,	1998;	Lovins,	Henly,	Ruderman,	&	Levine,	1988;	Schipper	&	
Grubb,	 2000).	 Even	 some	 of	 the	 researchers	 that	 argue	 towards	 the	 impact	 of	 the	 rebound	 effect	
acknowledge	that	for	specific	energy	services,	complete	offset	could	decline	as	demand	saturates,	(Sorrell,
2. Energy	use	and	sustainability	
	
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2007).	 As	 such,	 reducing	 energy	 use	 at	 home	 by	 improved	 technological	 solutions	 might	 be	 insufficient	
without	the	cooperation	of	individuals,	since	the	use	of	energy	at	home	results	from	a	complex	interaction	
between	built	form,	location,	energy-using	appliances,	occupants	and	the	affordability	of	fuel,	(Crosbie	&	
Baker,	2010).		
2.3 	Concluding	remarks	
This	chapter	looked	at	characteristics,	(RQ1a)	and	determinants,	(RQ1b),	of	energy	use,	showing	that	there	
is	a	growing	trend	in	energy	use	and	a	multitude	of	reasons	that	shape	and	influence	energy	use	at	home,	
(RQ2).		
A	 distinctive	 characteristic	 of	 energy	 use	 at	 home,	 (RQ1a),	 could	 be	 seen	 in	 its,	 ‘invisibility’,	 as	 a	
characteristic	in	itself,	further	expressed	through	energy	entering	homes	through	hidden	pipes,	or	by	the	
nature	 of	 current	 metering	 and	 billing	 systems,	 (Burgess	 &	 Nye,	 2008;	 Darby,	 2006;	 Hargreaves,	 2012).	
Energy	is	not	used	directly	at	home	but	rather	mediated	by	the	appliances	people	have	and	the	practices	
people	do	at	home,	such	as	cooking,	lighting,	or	washing	for	example,	(Martiskainen,	2007).	A	second	key	
characteristic,	(RQ1a),	is	the	common	understanding	of	energy	being	something	essential	for	people	to	live	
in	the	way	we	know	and	that	it	is	considered	almost	as	a	given	that	is	normal	to	have,	or	at	least	to	use	the	
services	and	amenities	that	it	provides,	(Geller	et	al.,	2006;	Sorrell,	2007).	With	this,	it	could	also	be	seen	
that	energy	might	be	an	intermediary	between	our	needs	and	the	fulfilment	of	those	needs.	
It	 also	 could	 be	 seen	 that	 there	 are	 numerous	 determinants	 that	 impact	 energy	 use	 that	 result	 from	 a	
mixture	 of	 socio-economical-techno-cultural	 factors	 that	 frame	 needs,	 opportunities,	 belief	 systems	 and	
abilities,	as	illustrated	in	Figure	2-3.	With	this,	it	could	be	seen	that	determinants	of	energy	use,	(RQ1b),	are	
frequently	a	result	of	enabling	variables	and	existing	conditions	where	a	number	of	factors	influence	the	
consumers’	 behaviours	 and	 emerging	 practices,	 (EEA,	 2013).	 Determinants	 that	 the	 literature	 provided	
include,	(RQ1b),	social	and	cultural	influences,	comfort,	convenience	and	needs,	norms,	and	technological	
developments,	as	well	as	economic	and	demographic	trends,	(Abrahamse	et	al.,	2005;	BPIE,	2011;	DGGE/IP-
3E,	 2004;	 Goldblatt,	 2005;	 INE	 I.P./DGEG,	 2011;	 Lomas,	 2010;	 Spaargaren	 &	 van	 Vliet,	 2000;	 Wilhite	 &	
Lutzenhiser,	 1999).	 It	 could	 be	 seen,	 for	 example,	 that	 technological	 development	 in	 buildings	 and	
appliances	 allows	 for	 increased	 efficiency,	 though	 a	 growth	 in	 the	 number	 of	 such	 technologies	 equally
2. Energy	use	and	sustainability	
	
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leads	to	an	increase	in	energy	demand	and	overall	energy	consumption,	a	situation	commonly	referred	to	
as	 the	 rebound	 effect,	 (Energy	 Saving	 Trust,	 2011;	 Khazzoom,	 1980).	 It	 also	 could	 be	 seen	 that	
infrastructure-social-cultural	settings	can	act	in	a	way	that	locks	people	into	their	building	infrastructure	
and	 behaviours,	 (Maréchal,	 2010).	 In	 this	 regard	 research	 to	 date	 indicates	 that	 buildings	 hold	 great	
potential	for	energy	saving,	yet	their	service	life	and	reduced	refurbishment	rates	may	require	more	time	to	
support	more	energy	efficient	lifestyles,	(BPIE,	2011;	Odyssee	&	MURE,	2011).	An	overall	increase	in	income	
levels,	 (Energy	 Saving	 Trust,	 2011),	 needs,	 (Lehman	 &	 Geller,	 2004),	 as	 well	 as	 an	 increasing	 number	 of	
single	households,	further	increases	total	energy	consumption,	(Energy	Saving	Trust,	2012;	Goldblatt,	2005).	
All	 of	 these	 factors	 are	 considered	 to	 contribute	 to	 an	 increase	 in	 energy	 use,	 or	 to	 the	 take	 back	 of	
efficiency	improvements	achieved	during	the	past	few	years,	(Odyssee	&	MURE,	2011),	also	known	as	the	
‘energy	efficiency	gap’,	(Feenstra	et	al.,	2009).	For	southern	European	countries	it	can	also	be	seen	that	the	
poor	 quality	 of	 the	 building	 envelope	 results	 in	 a	 less	 efficient	 use	 of	 energy	 in	 order	 to	 maintain	 the	
required	level	of	thermal	comfort,	(Healy,	2003;	SEI,	2003).	
With	regards	to	how	people	perceive	their	energy	use	at	home,	(RQ1c),	a	number	of	different	aspects	could	
be	found	in	the	literature.	It	could	be	seen	that	people	perceive	their	energy	use	as	normal,	even	if	as	such	
it	 includes	 commodities	 that	 are	 indispensably	 necessary	 to	 support	 one’s	 life,	 but	 also	 those	 that	 are	
perceived	 as	 being	 ‘normal’,	 (Lehman	 &	 Geller,	 2004;	 Smith,	 1776;	 Townsend,	 1979,	 WWF,	 2012).	 The	
chapter	further	discusses	that	the	understanding	of	what	‘normal’	is,	is	perhaps	not	normal	at	all,	or	normal	
for	all	and	that	‘normal’	standards	can	be	defined	as	a	mix	of	individual	preferences	that	are	influenced	by	
social	common	understandings,	(Giddens,	1984;	Lewis,	1969).
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3 	Energy	use	behaviours:	motivations	and	barriers		
This	chapter	explores	the	nature	of	energy	related	behaviours	and	investigates	the	underlying	motivations	
and	barriers	that	can	encourage	the	adoption	of	more	energy	efficient	ones	(RQ2).	
3.1 	Motivations	for	saving	energy	at	home	
Saving	money	or	reducing	cost	is	commonly	reported	as	the	primary	motivation	for	saving	energy	at	home,	
(Leiserowitz	et	al.,	2009).	Besides	the	financial	motivation,	other	known	motivational	variables	include,	for	
example,	 the	 need	 to	 comply	 with	 social	 norms,	 or	 to	 comply	 with	 personal,	 altruistic	 and	 moral	
motivations	 such	 as	 environmental	 protection,	 (IPPR,	 2009;	 Leiserowitz	 et	 al.,	 2009).	 Leiserowitz	 et	 al.	
(2009)	 found	 for	 example,	 that	 such	 personal,	 altruistic	 and	 moral	 motivation	 for	 Americans	 can	 be	
translated	 into	 actions	 such	 as	 to	 turn	 off	 the	 lights,	 lowering	 the	 thermostat	 in	 winter,	 or	 raising	 it	 in	
summer.	In	line	with	this,	Brouwer	et	al.	(2008)	found	that	80	percent	of	Europeans	would	pay,	on	average,	
an	 extra	 one	 Euro	 per	 100	 Kilometre	 for	 their	 airline	 ticket	 out	 of	 a	 sense	 of	 moral	 obligation	 and	
responsibility,	with	respect	to	climate	change,	concern	for	future	generations	and	the	environment.	Yet,	
Kaplan	 (2000)	 found,	 for	 example,	 that	 personal,	 altruistic	 or	 moral	 motivations	 can	 also	 work	 in	 the	
opposite	way	and	cause	feelings	of	helplessness,	or	stressing	the	individual	sacrifice	and	thus	acting	as	a	
motivation	to	maintain	existing	energy	related	behaviours,	with	individuals	resisting	making	changes	that	
they	perceive	as	reducing	quality	of	life.	
3.2 	Pro-environmental	 concern:	 a	 motivational	 variable	 or	 barrier	 to	
behaviour?	
Research	 to	 date	 indicates	 that	 the	 majority	 of	 people	 in	 industrialized	 countries	 (1),	 are	 aware	 of	
environmental	 problems,	 (Diekmann	 &	 Meyer,	 2008;	 Leiserowitz,	 2007;	 Lorenzoni	 &	 Pidgeon,	 2006;	
Poortinga,	Pidgeon,	&	Lorenzoni,	2006)	(2),	hold	positive	attitudes	towards	environmental	protection	(3),	
are	aware	of	the	environmental	consequences	and	personal	risks	and	(4),	hold	information	regarding	ways
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on	how	to	tackle	the	problems,	(Brouwer,	Brander,	&	van	Beukering,	2008;	Eurobarometer;	2011a,	2011b;	
Maibach,	Roser-Renouf,	&	Leiserowitz,	2009;	Whitmarsh,	2009).	These	findings	together	suggest	that	pro-
environmental	behaviour	should	be	widespread	among	these	populations,	which	however	does	not	seem	
to	be	apparent.	Despite	such	positive	attitudes,	concerns	and	awareness,	these	do	not	seem	to	translate	
adequately	 into	 pro-environmental	 behaviours	 and	 thus	 there	 appears	 to	 be	 an	 attitude-behaviour	 gap,	
(Kollmuss	 &	 Agyeman,	 2002;	 Lehman	 &	 Geller,	 2004;	 Tobler	 et	 al.,	 2012),	 with	 people	 not	 behaving	 in	
accordance	to	their	attitudes	and	adopting	pro-environmental	and	energy	efficient	behaviours	at	home.	
Looking	at	the	literature	it	appears	however,	as	if	there	are	a	number	of	reasons	that	might	explain	this	
apparent	phenomenon.	
Firstly,	 environmental	 problems	 appear	 to	 be	 perceived	 as	 a	 less	 immediate	 threat	 within	 the	 limited	
capacity	 of	 individuals	 for	 worrying	 about	 an	 issue;	 a	 phenomenon	 known	 as	 the	 finite	 pool	 of	 worry,	
(Linville	&	Fischer,	1991).	As	the	level	of	worry	increases	about	one	type	of	risk,	concern	about	others	may	
decrease,	 with	 people	 tending	 to	 pay	 more	 attention	 to	 near-term	 threats,	 such	 as	 the	 economic	 crisis,	
rather	than	to	larger	and	long-term	threats,	such	as	climate	change,	(Leiserowitz,	Maibach,	Roser-Renouf,	
Smith,	 &	 Hmielowski,	 2011;	 Linville	 &	 Fischer,	 1991;	 Upham	 et	 al.,	 2009).	 Most	 recent	 data	 for	 Europe	
confirms,	for	example,	that	topics	such	as	climate	change	have	been	losing	importance,	whilst	at	the	same	
time,	anxiety	over	the	economy	rose,	(Eurobarometer,	2010;	Eurobarometer,	2011a:	2011b).		
Secondly,	 people	 are	 disconnected	 to	 environmental	 consequences,	 which	 are	 often	 evaluated	 as	
uncertain,	 as	 those	 risks	 are	 perceived	 as	 being	 spatially	 and	 temporarily	 remote	 risks,	 affecting	 future	
generations	and	other	countries,	(Maibach	et	al.,	2009;	Upham	et	al.,	2009;	APA,	2009).	Gilford	et	al.	(2008)	
described	this	issue	as,	“Temporal	pessimism”	and,	“Spatial	optimism”.	“Temporal	pessimism”,	means	that	
environmental	 quality	 will	 decrease	 over	 time,	 whereas,	 “Spatial	 optimism”,	 implies	 that	 environmental	
quality	worsens	as	geographic	distance	increases.	Research	to	date	suggests	that	there	is	one	exception	to	
this	 ranking	 of	 individual	 concerns;	 energy	 security.	 For	 example,	 DECC	 (2012),	 found	 that	 in	 general,	
concern	about	energy	security	to	be	higher	than	concern	about	climate	change	and	that	40	percent	of	those	
surveyed	were	concerned	with	steep	rises	in	energy	prices.
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Thirdly,	 understanding	 environmental	 issues	 is	 a	 complex	 topic	 and	 there	 is	 noticeable	 doubt	 about	 the	
validity	of	scientific	findings,	such	as	climate	change	and	the	degree	of	anthropomorphic	contribution	to	it,	
(BBC	News,	2010;	IPPR,	2009;	Leiserowitz	et	al.,	2011a;	Reynolds,	Bostrom,	Read,	&	Morgan,	2010).	This	
complexity,	 in	 conjunction	 with	 individual	 detachment,	 to	 the	 topic	 can	 lead	 to	 a	 perceived	
disempowerment	 and	 belief	 that	 individuals	 cannot	 do	 anything,	 or,	 are	 not	 responsible	 for	 solving	 the	
problem,	(Brouwer	et	al.,	2008;	Martiskainen,	2007;	S.C.	Moser	&	Dilling,	2004;	Whitmarsh,	2009).		
Fourthly,	engaging	in	some	type	of	pro-environmental	behaviours	can	provide	a	feeling	of	having	done	their	
bit,	regardless	of	the	limited	impact	their	actions	might	actually	have,	which	then	can	result	in	ascribing	
further	 responsibility	 to	 others	 to	 take	 additional	 actions,	 (Prendergrast	 et	 al.,	 2008).	 Weber	 (1997)	
described	this	as	the	“Single	action	bias”,	representing	the	tendency	individuals	have	to	engage	in	single	
corrective	actions,	making	them	less	likely	to	take	additional	steps	if	the	first	action	is	not	the	most	effective	
one	 and	 presumably,	 because	 the	 first	 action	 succeeded	 in	 reducing	 their	 feeling	 of	 ”Worry	 or	
vulnerability”.	In	addition	to	this,	feeling	responsible	for	solving	the	problem	can	be	influenced	by	time	and	
space	 where	 individuals	 pay	 more	 attention	 to	 near-term	 threats	 and	 care	 for	 their	 family	 and	 friends,	
(Slovic,	2000;	Slovic,	Finucane,	Peters,	&	MacGregor,	2004;	Weber,	2006).	Such	responsibility	to	care	for	
becomes	looser	once	discussing	future	generations	or	more	abstract	locations,	such	as	the	nation,	or	the	
world.	Following	the	time/space	phenomenon	and	the	resulting	individual	detachment,	immediate	threats	
such	as	a	shortage	in	energy	supply	are	more	relevant	and	of	greater	urgency	than	future	problems,	for	
example	climate	change,	(Slovic,	2000;	Slovic	et	al.,	2004;	Weber,	2006).		
Lastly,	 this	 understanding	 of	 shared	 responsibility	 in	 solving	 the	 problem	 implies	 a	 need	 for	 a	 collective	
effort,	(Leal	Filho,	2011)	and	where	free-riders	can	cause	a	lack	of	collective	motivation	to	act	more	pro-
environmentally.	 Free-riders	 are	 usually	 individuals	 who	 are	 extremely	 resistant	 to	 changing	 their	 own	
actions	and	instead	enjoy	the	benefit	accrued	from	collective	effort,	but	contribute	little	or	nothing	to	the	
effort	of	achieving	the	common	goal,	(IPPR,	2009;	Maibach	et	al.,	2009;	Upham	et	al.,	2009).	Common	free-
riders	within	an	environmental	context	include,	all	others,	other	countries	and	the	enterprise	sector,	with	
examples	for	the	latter	being	shopping	centres	that	leave	their	lights	on	all	night,	or	distant	activities,	such	
as	engaging	in	deforestation	outside	of	national	boundaries.	As	Garvey	(2009)	summarized,	“The	sea	level
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will	 be	 where	 it	 will	 be	 in	 2050	 whether	 this	 wine	 bottle	 is	 recycled	 or	 not.	 So	 why	 bother?”.	 Such	 a	
conscious	 denial	 of	 personal	 responsibility	 is	 also	 known	 as	 the	 “Passive	 bystander”	 effect,	 (Marshall	 &	
Lynas,	 2003),	 or	 “Bystander	 effect”,	 (Darley	 &	 Latane,	 1968)	 and	 can	 reflect	 low	 individual	 efficacy	 on	
contributing	towards	solving	the	problem,	(Lorenzoni	&	Pidgeon,	2006;	Upham	et	al.,	2009).	The	passive	
bystander	effect	expresses	the	way	in	which	individual	responses	are	influenced	by	the	responses	of	those	
around	 them.	 Previous	 experience	 demonstrated	 the	 individuals’	 tendency	 to	 social	 conformity	 and	 the	
social	influence	from	family,	friends	or	neighbours,	which	might	be	illustrated	as	“If	others	don’t	do	it,	it’s	
rather	not	important,	so	why	should	I	care”,	(Thaler	&	Sunstein,	2008).	This	is	to	say	that	individuals	hold	
low	expectations	about	the	impact	of	their	own	actions,	but	at	the	same	time,	they	strongly	believe	that	if	a	
large	number	of	individuals	would	engage	in	those	same	actions	then	that	would	have	an	impact	and	could	
solve	the	problem,	(Maibach	et	al.,	2009).	But	by	doing	this	it	also	increases	the	feeling	that	individuals’	
actions	do	not	make	a	difference	on	their	own.	The,	free-rider,	problem	is	therefore	one	where,	what	as	a	
group	could	be	called	a	rational	response,	meaning	to	take	action,	becomes	irrational	for	an	individual,	if	no	
other	bystander	seems	to	have	any	intention	to	act;	the	idea	of	“I	will	if	you	will”.	The,	free-rider,	problem	
connects	to	the,	“Tragedy	of	the	commons”,	dilemma,	(Hardin,	1968;	Jager,	Janssen,	Vries,	Greef,	&	Vlek,	
2000)	in	which	the	behaviour	that	is	in	the	individual’s	interest	is	not	optimal	from	the	group’s	aggregate	
perspective	and	vice	versa.	This	is	where	multiple	individuals,	acting	independently	and	rationally	in	their	
own	 self-interest,	 ultimately	 deplete	 a	 shared,	 limited,	 resource,	 even	 once	 it	 is	 clear	 that	 it	 is	 not	 in	
anyone's	 long-term	 interest.	 This	 can	 lead	 to	 a	 feeling	 of	 powerlessness,	 since	 if	 people	 perceive	 they	
cannot	change	a	situation	they	will	very	likely	retreat	into	apathy	and	resignation	and	thus	will	be	less	likely	
to	 address	 environmental	 issues,	 (Kollmuss	 &	 Agyeman,	 2002;	 S.	 C.	 Moser,	 2007;	 S.	 C.	 Moser	 &	 Dilling,	
2004).	
As	such	there	appears	to	be	a	wealth	of	literature	findings	that	explains	why	positive	attitudes,	concerns	
and	 awareness	 regarding	 the	 environment	 might	 not	 result	 in	 pro-environmental	 and	 energy	 efficient	
behaviours	at	home.
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3.3 	Barriers	to	adopting	more	energy	efficient	behaviours	
In	 accordance	 with	 the	 literature	 there	 appears	 to	 be	 a	 number	 of	 barriers	 that	 could	 influence	 the	
adoption	 of	 more	 energy	 efficient	 behaviours.	 Even	 where	 individuals	 are	 concerned	 about	 the	
environment,	or	are	motivated	to	save	money	by	reducing	their	energy	use,	the	adoption	of	more	energy	
efficient	 behaviours	 can	 often	 have	 negative	 connotations	 associated	 with	 giving	 up	 something,	 a	
discomfort,	 a	 restricted	 lifestyle,	 or	 a	 more	 general	 reduction	 in	 their	 quality	 of	 life,	 (Barenergy,	 2011;	
Kaplan,	2000).	
3.3.1 	Monetary	focus	as	a	barrier	
A	focus	on	saving	money	as	a	motivation	to	save	energy	might	ultimately	form	a	barrier,	for	the	following	
reasons.	Firstly,	a	focus	on	saving	money	can	contribute	to	feelings	of	boringness	and	hassle,	caused	by	the	
effort	required	to	engage	in	numerous	actions,	that	at	the	end	of	the	day	result	in	only	minor	monetary	
savings,	(Green	Alliance,	2011;	IPPR,	2009).	Secondly,	a	focus	on	saving	money	could	lead	to	the	rebound,	
or	take	back	effect	(see	section	2.2.8.).	Thirdly,	for	most	households,	except	those	in	fuel	poverty,	energy	
bills	account	for	a	small	(3-4	percent)	share	of	disposable	income,	which	might	result	in	a	lack	of	motivation	
for	people	to	take	meaningful	actions	to	save	energy	at	home,	(BPIE,	2011).	As	such,	money	as	a	motivation	
to	less	energy	use	appears	to	be	a	barrier	towards	actually	realizing	energy	savings.	
3.3.2 	External/macro	barriers:	policy	based,	structural	and	economic	barriers		
The	literature	posits	that	there	are	a	number	of	external/macro	barriers,	namely	policy	based,	structural	
and	economic	barriers	that	can	influence	energy	use	at	home.	Politicians	develop	frameworks,	such	as	laws,	
directives	or	regulations,	which	can	facilitate,	or	work	as	a	barrier	to,	the	adoption	of	more	energy	efficient	
behaviours,	 (Barenergy,	 2011).	 Policy	 making	 can	 organise	 opportunities	 to	 foster	 innovation	 and	
technology	take-up,	but	also	to	set	the	ground	for	promoting	pro-environmental	behaviours,	or	to	prohibit	
those	behaviours	that	are	not	in	the	interest	of	the	individuals	or	the	society,	(Green	Alliance,	2011).	The	
introduction	of	congestion	charges	and	the	defining	of	standards	for	buildings	and	electrical	appliances,	are	
examples	 for	 how	 policy	 based	 interventions	 can	 influence	 the	 adoption	 of	 more	 energy	 efficient	
behaviours.	Policy	based	interventions	can	however	also	create	a	barrier.	If	charges	and	standards	are	set
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too	low,	they	might	not	have	much	influence	with	regards	to	behavioural	change,	but	rather	work	as	an	
indicator	of	what	is	socially	expected.	An	example	for	this	would	be	the	current	policy	attempts	to	assure	
that	 energy	 supply	 would	 always	 match	 growing	 demand;	 where	 energy	 intensive	 behaviours	 are	 not	
challenged,	but	rather	accepted	and	supplied,	(Green	Alliance,	2011).		
Further	 to	 this,	 physical-structural	 barriers,	 such	 as	 the	 available	 infrastructure	 of	 the	 buildings,	 or	 the	
availability	 and	 economic	 viability	 of	 technological	 solutions,	 also	 influence	 the	 degree	 of	 freedom	 and	
opportunity	to	adopt	more	energy	efficient	behaviours,	(Barenergy,	2011).	Such	physical-structural	barriers	
can	lead	to	so	called	locked-in	situations,	such	as	being	locked	into	poorly	built	and	inefficient	housing,	
(Goldblatt,	 2005;	 Maréchal,	 2010;	 Martiskainen,	 2007).	 Overcoming	 physical-structural	 barriers	 thus	
requires	refurbishment	of	older	housing	and	making	available	new	physical-structural	infrastructures,	such	
as	the	introduction	of	more	energy	efficient	products.	Removing	physical-structural	barriers	does	however	
not	necessarily	lead	to	realizing	energy	savings	due	to,	for	example,	rebound	and	take	back	effects,	or	due	
to	the	energy	efficiency	gap,	(Maibach	et	al.,	2009).	
In	 addition	 to	 this	 there	 might	 also	 be	 economic	 barriers,	 such	 as	 required	 initial	 investment,	 or	 the	
capability	 and	 willingness	 to	 invest,	 (Barenergy,	 2011),	 that	 can	 play	 a	 crucial	 role	 in	 this	 and	 act	 as	 a	
disincentive	 to	 adopt	 more	 energy	 efficient	 behaviours,	 (IPPR,	 2009).	 With	 regard	 to	 these,	 there	 also	
appears	to	be	a	preference	of	short-term	gains	compared	to	long-term	ones,	(Nordlund	&	Garvill,	2002,	
2003;	 Stern,	 2000;	 Thøgersen	 &	 Ølander,	 2002),	 as	 well	 as	 a	 preference	 for	 action	 when	 these	 create	
potential	 gains,	 rather	 than	 taking	 action	 to	 avoid	 potential	 losses,	 (Tversky	 &	 Kahneman,	 1991).	 For	
example,	 one	 might	 prefer	 to	 refurbish	 the	 kitchen	 that	 results	 in	 immediate	 benefits,	 rather	 than	 to	
exchange	the	boiler	for	a	more	energy	efficient	one	so	as	to	save	money	in	the	medium-long	term.	More	
environmentally	 friendly	 options	 are	 often	 also	 more	 expensive	 than	 standard	 appliances	 or	 services,	
(Barenergy,	2011)	and	thus	constitute	an	additional	barrier,	(Leiserowitz	et	al.,	2009).	Economic	barriers	
thus	 perhaps	 influence	 efficiency	 behaviours	 more	 strongly	 than	 curtailment	 ones,	 since	 curtailment	
behaviours	often	do	not	require	an	investment.	In	addition	to	this,	home	appliances	may	have	long	lifetime	
spans	 and	 are	 purchased	 infrequently.	 As	 a	 result	 substituting	 them	 might	 not	 always	 be	 beneficial	 in	
environmental	terms	and	would	require	complex	calculations	outside	the	ability	of	most	ordinary	people,	
(DGGE/IP-3E,	2004;	Leiserowitz	et	al.,	2009;	Quercus,	2008).	Addressing	economic	barriers	has	thus	proved
3.	Energy	use	behaviours:	motivations	and	barriers	
	
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to	be	a	challenging	topic	that	might	require	governmental	interventions,	such	as	homeowner	tax	breaks	and	
subsidy	 programmes,	 to	 support	 and	 accelerate	 the	 diffusion	 of	 more	 energy	 efficient	 appliances	 and	
solutions,	(Leiserowitz	et	al.,	2009).	
3.3.3 	Knowledge	based	barriers	
Lack	 of	 individual	 knowledge	 can	 also	 constitute	 a	 barrier	 for	 the	 adoption	 of	 more	 energy	 efficient	
behaviour	since	they	might	not	know	how	to	behave	more	efficiently,	or	do	not	have	the	time	to	research	
which	options	are	best,	(Leiserowitz	et	al.,	2009).	Knowledge	based	barriers	are	associated	with	a	lack	of	
access,	 or	 difficulty	 in	 understanding	 relevant	 information,	 such	 as	 regarding	 different	 options	 and	 the	
potential	benefits	of	those	different	options,	(Barenergy,	2011;	Leiserowitz	et	al.,	2009).	Information	might	
entail	accessing	different	sources,	from	a	more	structural	level,	such	as	fiscal,	legal,	regulatory,	to	a	more	
individual	level	of	cost,	awareness,	or	benefits.	Previous	research	indicates	however,	that	there	appears	to	
be	a	good	level	of	knowledge	regarding	topics	such	as	the	contributions	of	behaviour	to	causes,	impacts	and	
solutions	 of	 climate	 change,	 (Brouwer	 et	 al.,	 2008;	 Eurobarometer,	 2011b;	 Whitmarsh,	 2009).	 These	
findings	equally	show	that	levels	of	knowledge	and	engagement	decrease	once	the	context	moves	from	
climate	 change	 to	 more	 specific	 issues,	 such	 as	 carbon	 reduction,	 or	 energy	 use,	 (Baird	 &	 Brier,	 1981;	
DEFRA,	2007;	Gatersleben,	2000;	Upham	et	al.,	2009;	Whitmarsh	et	al.,	2009).	These	decreasing	levels	of	
knowledge	might	thus	be	a	barrier	for	what	the	individual	understands	to	be	links	between	behaviour	and	
lifestyle	at	home	and	increase	in	energy	use,	carbon	consumption	and	CO
2
	emissions,	(Brandon	&	Lewis,	
1999;	 Darby,	 2006;	 Upham	 et	 al.,	 2009;	 Future	 Foundation,	 2006).	 In	 addition	 to	 this	 previous	 research	
suggests	that	there	is	low	salience	of	climate	change,	energy	and	environment	in	individuals’	day-to-day	
choices	and	actions,	(Brook	Lyndhurst,	2007;	Giorgi,	Fell,	Austin,	&	Wilkins,	2009).	This	highlights	a	potential	
dissonance	between	the	growing	knowledge	and	awareness	of	environmental	problems	at	a	general	level,	
that	does	not	translate	into	personally	relevant	behaviours	and	thus	constitutes	an	information-behaviour	
gap,	(Energy	Saving	Trust,	2011;	Martiskainen,	2007).	Previous	studies	in	Portugal	equally	reveal	a	lack	of	
information	regarding	the	most	relevant	energy	uses	at	home	in	terms	of	their	relative	proportion	to	the	
monthly	 energy	 bill,	 which	 indicates	 a	 dissonance	 between	 the	 actual	 and	 the	 perceived	 energy	 use	 of	
different	categories	of	home	appliances,	(Quercus,	2008).
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3.3.4 	Cultural	–	normative	and	social	barriers	
Cultural	prerequisites	and	social	norms	that	set	aesthetics,	comfort	or	even	social	position,	can	also	work	as	
barriers	 towards	 adopting	 more	 energy	 efficient	 lifestyles,	 (Barenergy,	 2011).	 To	 resolve	 such	 barriers	
requires	 a	 clear	 understanding	 about	 the	 social	 processes	 within	 which	 decisions	 are	 made,	 (Carpenter,	
Folke,	Scheffer,	&	Westley,	2009;	Folke,	2006).	Energy	saving	behaviour	challenges	existing	ways	of	thinking	
and	doing,	including	social	customs	and	the	ways	of	living,	as	well	as	the	assumptions	that	support	these	
attitudes	and	behaviours,	(Sedgwick	and	Edgar,	1999).	Within	current	lifestyles,	most	of	the	energy	related	
services	 are	 perceived	 as	 necessary	 for	 meeting	 basic	 needs	 and	 social	 practices.	 Therefore,	 energy	
consumption	 has	 been	 driven	 by	 evolving	 expectations	 and	 standards	 of	 what	 is	 normal,	 (Heiskanen,	
Johnson,	&	Vadovics,	2009;	Quitzau	&	Røpke,	2008;	Shove,	2003).	Examples	of	such	evolving	practices	and	
norms	are	plenty,	including	the	aesthetics	question	of	solar	panels,	(IPPR,	2009),	to	energy	efficient	lighting,	
(Leiserowitz	 et	 al.,	 2009),	 the	 social	 taste	 for	 ambient	 low-lighting,	 (Barenergy,	 2011;	 Southerton	 et	 al.,	
2011;	Wilhite	&	Lutzenhiser,	1999),	or	the	importance	of	evolving	cooling	(and	heating),	practices	at	home,	
(Shove,	2005;	Wilhite	and	Ling,	1992).	These	cultural,	normative	and	social	settings	help	to	frame	normal	
behaviour	and	expectations	concerning	the	consumption	of	energy	and	therefore,	work	as	a	barrier	to	the	
adoption	of	energy-saving	behaviours,	(Southerton	et	al.,	2011).	Therefore,	energy	consumption	might	not	
only	 be,	 individually	 invisible,	 but	 also,	 socially	 invisible	 and	 rarely	 the	 subject	 of	 conscious	 decision,	
(Lutzenhiser,	 1993).	 Changing	 these	 social	 customs	 and	 norms	 is	 both	 difficult	 and	 problematic,	 as	 it	
requires	shifting	the	focus	of	intervention	away	from	individual	consumer	decisions,	toward	shaping	and	
intervening	in	the	shared	behaviours	of	social	groups,	(Southerton	et	al.,	2011).	
3.4 	Individual	psychological	barriers	
Individual	psychological	barriers	are	the	product	of	the	existing	cultural,	normative	and	social	expectations	
that	support	the	individual	perception	regarding	limits	to	what	people	are	willing	to	do	to	save	energy,	with	
these	limits	often	being	rooted	in	personal	experiences,	or	upbringing,	(Barenergy,	2011).	In	this	context	
psychological	 barriers	 can	 help	 to	 explain	 an	 existing	 unwillingness	 to	 adopt	 more	 energy	 efficient	
behaviour	and	thus	constitute	barriers	and	as	further	examined	in	the	following.
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3.4.1 	Habits	as	a	barrier		
Energy	use	at	home	is	often	the	outcome	of	established	habits	and	practices	that	can	constitute	a	barrier	
towards	the	adoption	of	different	and	more	energy	efficient	behaviours,	(Darnton,	2008;	Jackson,	2005;	
Martiskainen,	2007;	Prendergrast	et	al.,	2008;	Upham	et	al.,	2009).	Habits	thus	can	act	as	a	determinant	of	
domestic	energy	use	and	are	seen	to	be	one	of	the	reasons	why	energy	consumption	keeps	rising	despite	
an	evident	increase	in	awareness	and	concern	about	energy	use	at	home,	(Maréchal,	2010).	Indeed,	energy	
consuming	behaviours,	such	as	switching	off	the	lights,	or	turning	off	appliances,	are	often	guided	by	deeply	
ingrained	habits	and	therefore	can	become	counter-intentional	to	individual	best	intents,	(Verplanken	&	
Faes,	1999).	Counter-intentional	habits	represent	a	kind	of	cognitive	trap,	that	locks	individuals	into	routine	
behaviours,	 even	 when	 these	 behaviours	 conflict	 with	 the	 individual’s	 rational	 deliberations,	 or	 that	 are	
inconsistent	 with	 social	 norms,	 (Jackson,	 2005).	 Counter-intentional	 habits	 might	 thus	 help	 explain	 the,	
efficiency	paradox	and	continued	increase	of	energy	consumption	despite	rising	environmental	awareness	
among	the	population,	(Maréchal,	2010).	Such	deeply	ingrained	habits	could	lead	to	locked-in	practices,	
where	individuals	become	locked-in	into	their	daily	energy	consumption	behaviours,	(Maréchal,	2010).	This	
makes	them	less	open	to	rational	deliberation	and	thus	cryptic	to	understand,	which	limits	the	individual’s	
response	 to	 policies,	 as	 well	 as	 behavioural	 change	 interventions,	 designed	 to	 promote	 the	 adoption	 of	
more	energy	efficient	behaviour,	(Jackson,	2005;	Stern,	2007).	As	a	result,	habits	can	become	behaviours	
that	 are	 difficult,	 (Bamberg,	 2003),	 although	 not	 impossible	 to	 change,	 (Matthies,	 Klöckner,	 &	 Preißner,	
2006).	
3.4.2 	Comfort	as	a	psychological	barrier	
The	expectation	of	individual	comfort	is	considered	to	be	an	important	psychological	barrier	to	any	attempt	
to	reduce	energy	consumption,	(Huebner,	Cooper,	&	Jones,	2011;	Shove,	2003).	The	distant	and	sometimes	
invisible,	negative	consequences	of	environmentally	damaging,	or	energy	intensive	behaviours,	seem	to	be	
overpowered	by	the	relatively	immediate	certainties	of	a	reduction	in	comfort	and	convenience,	(Lehman	&	
Geller,	2004).	Understanding	the	detail	to	what	constitutes	comfort	requires	one	to	consider	contextual,	
social,	 technological,	 cultural,	 historical	 and	 psychological	 factors,	 (Hitchings,	 2009;	 Shove,	 2003,	 2006).	
Recent	 trends	 suggest	 a	 large	 variation	 in	 comfort	 conditions	 and	 practices,	 (de	 Dear	 &	 Brager,	 2001;
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Hitchings,	2009),	but	also	a	decreased	level	of	individual	thermal	adaptability	due	to	the	growing	attraction	
of	setting	unsustainable	ambient	standards,	(de	Dear	&	Brager,	2001).	In	global	terms,	the	energy	cost	of	
maintaining	standardized	comfort	conditions	in	buildings	and	in	indoor	environments	around	the	world	is	
ultimately	 unsustainable,	 (Shove,	 Heather,	 Lutzenhiser	 &	 Hacket,	 2008).	 Although	 people	 have	 reported	
being	comfortable	in	a	temperature	range	of	6	–	30
o
C,	(Chappells	and	Shove,	2005),	comfort	expectations	
are	converging	towards	artificially	heated	and	cooled	environments,	which	increase	energy	and	resource	
use,	 particularly	 as	 air-conditioning	 gains	 prominence	 in	 households,	 (Cooper,	 1998;	 Ackermann,	 2002).	
Today	most	people	tolerate	a	narrower	temperature	band	and	reject	former	ways	of	achieving	comfort,	
such	as	opening	windows,	using	blankets	and	appropriate	clothing,	building	thermally	efficient	housing,	or	
taking	siestas	on	hot	afternoons,	(Shove,	2003).	Therefore	expectations	about	what	type	of	thermal	comfort	
is	 desirable	 (humidity	 levels,	 temperature,	 etc.),	 as	 well	 as	 how	 that	 comfort	 should	 be	 achieved,	 are	
converging	 towards	 air-conditioned	 environments,	 (Strengers,	 2008).	 Despite	 the	 direct	 link	 between	
comfort,	peak	demand	and	demand	management,	current	expectations	of	comfort	are	still	considered	to	
be	 a	 basic,	 non-negotiable	 human	 right	 in	 developed	 nations,	 rather	 than	 being	 understood	 as	
unsustainable,	(Strengers,	2008).	
3.4.3 	Individual	beliefs	and	self-efficacy	as	a	barrier	
An	individual’s	belief	about	the	ease	or	difficulty	of	performing	a	given	behaviour,	or	on	being	capable	of	
achieving	 a	 particular	 goal,	 is	 seen	 to	 influence	 individual	 decision	 on	 whether	 or	 not	 to	 conduct	 a	
behaviour,	(Martiskainen,	2007).	From	literature	this	belief	has	been	observed	in	studies	on	self-efficacy	
expectancies,	(Bandura,	1986),	perceived	behavioural	control,	(Ajzen	&	Madden,	1986),	locus	of	control,	
(Maddux,	1995),	ability	concepts,	(Ølander	&	Thøgersen,	1995),	or	sense	of	agency,	studies,	(Jeannerod,	
2003).	Such	studies	all	show	that	one’s	behaviour	can	have	an	impact	and	that	one	is	capable	of	controlling	
the	 outcomes	 of	 one’s	 own	 behaviour.	 This	 involves	 both	 beliefs	 about	 the	 likelihood	 between	 certain	
behaviours	and	desired	goals	or	outcomes	(outcome	expectancies)	and	beliefs	about	an	individual’s	ability	
to	execute	the	behaviours	(self-efficacy	expectancies).	In	his	original	work	Bandura	(Figure	3-1)	referred	to	
such	a	distinction	as	“Efficacy	expectations”	and	“Outcome	expectations”	with	the	former	meaning	“The
3.	Energy	use	behaviours:	motivations	and	barriers	
	
43	
conviction	that	one	can	successfully	execute	the	behaviour	required	to	produce	outcomes”	and	the	latter	as	
“A	person’s	estimate	that	a	given	behaviour	will	lead	to	certain	outcomes”,	(Bandura,	1977a,	p.	193).	
	
Figure	3-1:	Diagrammatic	representation	of	the	conditional	relations	between	efficacy	beliefs	and	outcome	
expectancies	(adapted	from	Bandura	(1977b),	p.	350).	
Bandura	 justifies	 this	 distinction	 on	 the	 ground	 that	 “Individuals	 can	 believe	 that	 a	 particular	 course	 of	
action	will	produce	certain	outcomes,	but	if	they	entertain	serious	doubts	about	whether	they	can	perform	
the	 necessary	 activities	 such	 information	 does	 not	 influence	 their	 behaviour”,	 (Bandura,	 1977a,	 p.	 350).	
Efficacy	beliefs	are	thus	seen	to	influence	the	initiation	and	persistence	of	behaviours	and	courses	of	action,	
thus	 they	 are	 assumed	 to	 be	 specific	 to	 behaviours	 and	 situations,	 (Bandura,	 1977a,	 1982,	 1986).	 As	 a	
consequence,	 perceived	 efficacy	 in	 one	 behavioural-situational	 domain	 could	 therefore	 be	 expected	 in	
other	domains	depending	on	the	extent	to	which	the	behaviours	and	situations	share	crucial	features	and	
require	similar	skills	and	functions,	(Bandura,	1990).	For	instance,	perceived	efficacy	in	recycling	might,	or	
might	not,	be	expected	to	occur	with	energy	saving	at	home,	depending	on	how	the	two	behaviours	are	
evaluated.		
Individual	beliefs,	 regarding	 self-efficacy,	 can	be	learned	in	various	ways,	including	personal	or	 vicarious	
experiences,	learning	influenced	by	individual	attempts	in	a	given	task,	the	degree	of	persistence	in	doing	so	
and	 ultimately	 success	 of	 the	 action,	 (Bandura,	 1977a).	 Bandura	 (1977a),	 hypothesized	 that	 self-efficacy	
affects	choice	of	activities,	effort	and	persistence	with	success,	or	failure,	in	personal	performance	being	
proposed	as	the	most	powerful	influence	on	self-efficacy.	Successful	personal	experiences	raise	self-efficacy	
and	failures	lower	it,	but	once	a	strong	sense	of	self-efficacy	is	developed,	a	failure	may	not	have	much	
impact,	(Bandura,	1986).	For	example,	if	someone	is	attempting	to	save	energy	and	registers	a	decrease	on	
the	 energy	 bill,	 this	 could	 contribute	 to	 the	 perception	 of	 self-efficacy	 via	 successful	 energy	 saving.	 The	
opposite,	 an	 increase	 on	 the	 energy	 bill,	 might	 contribute	 to	 belief	 failure	 and	 lack	 of	 efficacy	 in	 saving	
energy.	This	building	of	personal	experience	is	seen	to	be	particular	important,	since	people	tend	to	hold	
onto	beliefs	and	do	not	abandon	them,	even	after	receiving	contradictory	information,	(Anderson,	2007).	
Person Behaviour Outcome
EFFICACY	BELIEFS
Level
Strength
Generality
OUTCOME	EXPECTANCIES
Physical
Social
Self-evaluative
3.	Energy	use	behaviours:	motivations	and	barriers	
	
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Individuals	can	hold	many	beliefs	about	any	given	behaviour,	but	they	can	attend	to	only	a	relatively	small	
number	of	beliefs	at	any	given	moment	and	it	is	this	small	number	of	salient	beliefs	that	are	considered	to	
be	 the	 prevailing	 determinants	 of	 a	 person’s	 intentions
10
	 and	 behaviours,	 (Ajzen,	 1991).	 In	 the	 case	 of	
energy	 this	 could	 be,	 for	 instance,	 to	 decide	 between	 adding	 another	 layer	 of	 clothes	 or	 maintaining	 a	
higher	 room	 temperature	 for	 perceived	 comfort	 needs.	 This	 is	 to	 say	 that,	 if	 one’s	 previous	 experience	
reinforces	self-efficacy	in	saving	energy	at	home,	one	might	persist	in	the	effort.	In	the	case	of	failure	this	
might	lead	to	the	abandonment	of	further	attempts	to	save	energy	at	home.	
Once	individual	self-efficacy	and	competence	 are	extended	to	a	group	level,	a	collective	efficacy	can	be	
observed.	 Individual	 responses	 are	 not	 entirely	 independent	 of	 responses	 from	 others,	 from	 what	 is	
perceived	as	the	social	norm	and	therefore	a	sense	of	collective	efficacy	does	exist	where	individuals	can	
solve	 their	 problems	 and	 improve	 their	 lives	 through	 concerted	 effort,	 (Bandura,	 1986).	 Research	 by	
Andreasen	(1995)	further	revealed	that	there	might	be	a	perceived	lack	of	collective	capacity	that	together	
with	a	perceived	opposition	and	a	perceived	social	mandate,	can	constitute	the	key	reasons	for	individual	
inaction.	This	perceived	lack	of	capacity	might	thus	occur	once	the	target	audience	no	longer	believes	that	
they	can	carry	out	an	action	and	maintain	it,	(Bandura,	1977a,	1992;	Rotter,	1954;	Schwartz,	1977;	Stern,	
1999).	For	instance,	believing	one	has	no	control	over	climate	change	could	facilitate	mechanisms	such	as	
denial	and	work	against	pro-environmental	behaviours,	(Gifford,	Iglesias,	&	Casler,	2008).	Baker	and	Kirsch	
(1991)	found	that	once	people	anticipated	aversive	outcomes,	they	were	no	longer	willing	to	engage	in	a	
behaviour	that	may	produce	those	outcomes.	Their	linguistic	habit	is	to	say	that	they	cannot	perform	the	
behaviour	(low	self-efficacy),	rather	than	saying	that	they	will	not	perform	it.	This	then	might	overestimate	
the	prevalence	of	lack	of	efficacy	and	also	generate	apathy	and	an	increased	sense	of	helplessness	towards	
environmental	issues,	(Allen	&	Ferrand,	1999;	Donn,	1999;	Vandenbergh,	Barkenbus,	&	Gilligan,	2008).	
3.4.4 	Resistance	and	unwillingness	to	change	as	a	barrier	
Resistance	and	unwillingness	to	change	often	results	from	deeply	ingrained	habits,	existing	and	commonly	
accepted	standards,	or	social	norms,	such	as	maintaining	the	current	levels	of	comfort	and	wellbeing,	that	
																																																																				
10
	An	intention	is	what	one	says	one	plans	to	do.
3.	Energy	use	behaviours:	motivations	and	barriers	
	
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all	can	be	considered	as	a	barrier	towards	the	adoption	of	more	energy	efficient	behaviours,	(Barenergy,	
2011;	Darnton,	2008;	Darnton,	Verplanken,	White,	&	Whitmarsh,	2011;	EEA,	2013;	Gardner	&	Stern,	2008;	
Jackson,	2005;	Prendergrast,	Foley,	Menne,	&	Isaac,	2008;	Shove,	2003).	
Research	has	provided	some	evidence	for	a	number	of	behaviours	in	terms	of	how	willing	people	are	to	
engage	in	them	in	order	to	protect	the	environment.		They	found	that	individuals	are	generally	receptive	
towards	recycling	and	the	conservation	of	energy	at	home,	but	noted	considerably	resistance	to	changing	
personal	habits,	such	as	travelling,	(DEFRA,	2007;	Thomas	&	Sharp,	2013;	Tobler	et	al.,	2012;	Upham	et	al.,	
2009;	Whitmarsh,	2009;	Whitmarsh,	Turnpenny,	&	Nykvist,	2009;	Williamson,	Soebarto	&	Radford,	2010).	
Travel	 habits	 seem	 to	 be	 the	 hardest	 to	 change;	 personal	 resistance	 and	 unwillingness	 to	 change	 are	 a	
prime	barrier	for	this,	(Tobler	et	al.,	2012).	
3.5 	Concluding	remarks	
This	chapter	looked	at	what	influences	energy	use	at	home	(RQ2),	and	the	underlying	motivational	variables	
and	barriers	for	adopting	more	energy	efficient	behaviours.	As	can	be	seen,	maintaining	existing	energy	
related	behaviours	appears	to	outweigh	the	motivation	to	adopt	more	energy	efficient	ones	as	a	result	of	a	
number	of	macro,	knowledge	related,	cultural,	normative,	social	and	psychological	reasons,	that	constitute	
barriers	towards	change.	Even	motivations,	such	as	realising	monetary	savings,	ultimately	can	constitute	a	
barrier.	Potential	benefits	seem	to	directly	compete	with	the	effort	that	would	be	required	to	engage	in	the	
numerous	actions	required	to	actually	achieve	meaningful	savings,	(BPIE,	2011;	Green	Alliance,	2011;	IPPR,	
2009;	 Leiserowitz	 et	 al.,	 2009),	 as	 well	 as	 competing	 with	 a	 perceived	 loss	 in	 terms	 of	 desired	 level	 of	
comfort	and	wellbeing,	(Barenergy,	2011;	Darnton,	2008;	Darnton,	Verplanken,	White,	&	Whitmarsh,	2011;	
EEA,	2013;	Jackson,	2005;	Shove,	2003).	Other	motivations,	such	as	the	need	to	comply	with	social	norms,	
or	 to	 comply	 with	 personal,	 altruistic	 and	 moral	 motivations,	 do	 not	 appear	 to	 constitute	 an	 important	
motivation	to	adopting	more	energy	efficient	behaviours	at	home,	(IPPR,	2009;	Leiserowitz	et	al.,	2009).	
From	a	barrier	perspective,	all	such	factors	could	however	prevent	the	adoption	of	more	energy	efficient	
behaviours	(RQ2b).	This	seemed	to	be,	in	particular,	true	for	family	related	comfort	levels	where	there	is	
considerable	resistance	to	change	ingrained	behaviours	particularly	those	that	are	perceived	as	normal	and	
socially	acceptable,	(DEFRA,	2007;	Tobler	et	al.,	2012;	Upham	et	al.,	2009;	Whitmarsh,	2009;	Whitmarsh	et
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al.,	 2009).	 A	 barrier	 towards	 change	 frequently	 results	 from	 a	 resistance	 to	 making	 changes	 that	 are	
perceived	as	reducing	quality	of	life,	(Kaplan,	2000),	while	preference	is	given	to	easy	to	do	habits,	such	as	
switching	the	lights	off,	or	recycling,	(Thøgersen	&	Ølander,	2002).	
As	 can	 be	 seen	 through	 this	 chapter,	 barriers	 for	 adopting	 more	 energy	 efficient	 behaviours	 at	 home	
(RQ2b),	might	also	include	(1),	The	lock	in	effect	of	infrastructures	and	existing	social	conventions,	such	as	
comfort	 and	 convenience,	 (Heiskanen	 et	 al.,	 2009;	 Jackson,	 2005;	 Martiskainen,	 2007).(2);	 The	
attitude/value-behaviour	gap,	(Kollmuss	&	Agyeman,	2002).	(3);	The	disconnection	towards	environmental	
risks,	 concerns	 and	 problems	 which	 are	 overall	 perceived	 as	 spatially	 and	 temporarily	 uncertain,	
(Eurobarometer,	2011a;	2011b;	Leiserowitz	et	al.	2011a;	2011b,	Maibach	et	al.,	2009;	Upham	et	al.,	2009);	
(4),	Required	engagement	in	numerous	small	actions,	(Kates	et	al.,	2001;	Weber,	1997);	(5),	The	invisibility	
of	the	consequences	of	ones	actions,	(Thøgersen,	2005);	(6),	Social	dilemmas,	since	individual	efforts	are	
understood	as	useless	unless	others	participate	or	contribute	as	well,	(Kollock,	1998;	Maibach	et	al.,	2009;	
Thaler	 &	 Sunstein,	 2008;	 Uusitalo,	 1990);	 free-riding	 as	 a	 problem	 in	 itself	 and	 as	 a	 justification	 for	
resistance	to	change	ones	own	actions,	(IPPR,	2009;	Maibach	et	al.,	2009;	Upham	et	al.,	2009);	(7)	Political	
and	economic	barriers	that	could	promote	and	facilitate	the	adoption	of	more	energy	efficient	behaviours,	
(Green	 Alliance,	 2011);	 (8),	 Cultural-normative	 barriers	 as	 social	 practices	 influence	 energy	 consumption	
driven	by	evolving	expectations	and	standards	of	normal	everyday	life,	(Heiskanen	et	al.,	2009;	Quitzau	&	
Røpke,	2008;	Shove,	2003;	Southerton	et	al.,	2011);	or	(9)	Knowledge	based	barriers	as	individuals	may	not	
always	be	aware	of	the	environmental	impacts	of	behaviours,	or	benefits	of	changes	in	these	behaviours,	
(Baird	&	Brier,	1981;	Gatersleben,	2000),	including	lack	of	access	to	relevant	information,	(Barenergy,	2011;	
DEFRA,	2007;	Energy	Saving	Trust,	2011;	Leiserowitz	et	al.,	2009;	Martiskainen,	2007;	Upham	et	al.,	2009;	
Whitmarsh	et	al.,	2009).	
In	 terms	 of	 psychological	 barriers	 (RQ2c),	 it	 can	 be	 seen	 that	 adopting	 more	 energy	 efficient	 behaviour	
might	require	increasing	efficacy	expectations	and	outcome	expectations,	(Bandura,	1977a;	Martiskainen,	
2007).	Anticipating	aversive	outcomes,	be	it	low	or	undesired	impacts,	might	explain	why	people	report	not	
being	capable	to	perform	a	behaviour	(low	self-efficacy),	rather	than	saying	that	they	will	not	perform	it,	
(Baker	&	Kirsch,	1991).	This	then	might	generate	apathy	and	an	increased	sense	of	helplessness,	(Donn,	
1999),	or	a	reduced	participation	in	environmentally	significant	behaviours,	(Allen	&	Ferrand,	1999).	Thus	it
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can	 be	 seen	 that	 to	 successfully	 address	 environmental	 problems	 will	 require	 a	 collective	 effort	 and	
efficacy,	which	then	brings	along	the	psychological	barrier	of	“I	will	if	you	will”,	(Vandenbergh	et	al.,	2008).	
Further	It	can	be	seen	that	the	aspects	of	time	and	space,	and	short-term	(economic),	focus	can	lead	to	a	
lack	 of	 consideration	 for	 longer-term	 impacts	 /	 interconnections	 of	 actions	 and	 decisions,	 (Nordlund	 &	
Garvill,	2002,	2003;	Stern,	2000;	Thøgersen	&	Ølander,	2002).	Currently	there	appears	to	be	no	clear	data	
for	Portugal	on	whether	such	aspects	of	time	and	space,	short-term	focus	and	longer-term	impact	can	be	
observed.	
The	literature	provides	little	evidence	regarding	the	ability	of	values	and	attitudes	to	influence	the	amount	
of	energy	being	used	at	home.	For	the	case	of	values,	literature	indicates	that	values	have	a	loose	influence	
on	behaviour,	(Rohan,	2000),	affecting	behaviour	indirectly	through	specific	beliefs,	norms	and	intentions,	
(Feather,	1990;	Nordlund	&	Garvill,	2003;	Poortinga	et	al.,	2004),	though	value-action	gaps	could	also	be	
observed,	 (Verplanken	 &	 Holland,	 2002).	 Similarly,	 the	 contribution	 of	 attitudes	 as	 a	 predictor	 of	 pro-
environmental	 behaviours	 seems	 not	 to	 be	 well	 established,	 despite	 the	 existence	 of	 available	 studies,	
(Bamberg,	2003;	Geller,	1981;	McKenzie-Mohr	&	Smith,	1999;	Poortinga	et	al.,	2004;	Schultz	et	al.,	1995;	
Thøgersen,	2004).	As	seen	from	the	literature	there	might	also	be	an	attitude-behaviour	gap,	(Kollmuss	&	
Agyeman,	2002).	Though	attitudes	seem	to	guide	behaviour	for	those	cases	where	attitudes	are	strong	and	
where	 social	 and	 structural	 conditions	 support	 the	 behaviour,	 (Stern,	 2000),	 or	 for	 changing	 simple,	
repetitive,	low-cost	energy	saving	behaviours,	(Abrahamse	&	Steg,	2009;	Abrahamse	et	al.,	2005;	Black	et	
al.,	1985;	Heberlein	&	Warriner,	1983;	Stern,	1992),	as	well	as	for	having	the	financial	ability	to	perform	the	
behaviour,	 (Gatersleben,	 2000).	 This	 might	 be,	 in	 particular,	 problematic,	 since	 energy	 consuming	
behaviours	 are	 often	 habitual	 and	 therefore	 difficult	 to	 modify,	 (Bamberg,	 Ajzen,	 &	 Schmidt,	 2003),	
although	not	impossible	to	change,	(Matthies	et	al.,	2006).	It	thus	appears	that	to	encourage	the	adoption	
of	 more	 energy	 efficient	 behaviour	 would	 likely	 require	 overcoming	 a	 number	 of	 barriers,	 including	
individual	psychological	ones.	Altogether	this	would	therefore	imply	a	need	for	better	understanding	of,	for	
example,	the	social	processes	within	which	decisions	are	made,	(Barenergy,	2011;	Carpenter	et	al.,	2009;	
Folke,	 2006),	 or	 how	 the	 cultural,	 normative	 and	 social	 settings	 impact	 to	 frame	 normal	 behaviour,	
(Maréchal,	2010).
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4 	Energy	use	and	intervention	strategies	
This	chapter	looks	at	the	potential	effectiveness	of	change	interventions	within	the	field	of	energy	use	at	
home	(RQ3)	and	the	different	types	of	interventions	that	might	be	applied.		
Achieving	lasting	behavioural	change	appears	to	be	often	problematic	and	environmental	values,	beliefs	
and	attitudes	do	not	appear	to	have	a	significant	influence	on	energy	consumption,	(Martiskainen,	2007;	
Upham	et	al.,	2009).	Some	agreement	exists	that,	promoting	behavioural	change	requires	a	combination	of	
effort,	from	communication	to	policy	making,	to	reduce	the	various	barriers	that	exist	(IPPR,	2009).	To	date,	
most	 intervention	 strategies	 have,	 however,	 predominantly	 focused	 on	 voluntary	 behavioural	 change,	
rather	 than	 on	 changing	 contextual	 factors	 that	 can	 determine	 individual	 decisions,	 (Abrahamse	 et	 al.,	
2005;	 Jackson,	 2005).	 Contextual	 factors	 set	 the	 context	 where	 individual	 decisions	 are	 made	 and	
intervention	 strategies,	 that	 do	 include	 both	 voluntary	 behaviour	 change	 and	 contextual	 factors,	 might	
therefore	 increase	 the	 level	 of	 success	 in	 promoting	 lasting	 behavioural	 change,	 (Gärling	 et	 al.,	 2002).	
Common	contextual	factors	include	technological	developments,	economic	growth,	demographic	factors,	
institutional	factors	and	cultural	developments,	(Gatersleben	&	Vlek,	1998),	that	together,	shape	individual	
factors,	 such	 as	 motivations,	 opportunities	 and	 abilities,	 (Ølander	 and	 Thøgersen,	 1995).	 Findings	 from	
Abrahamse	et	al.	(2005),	suggest	that	once	voluntary	behaviour	change	and	contextual	factors	are	applied	
together,	then	behavioural	change	interventions	might	also	be	able	to	target	the	individual’s	perceptions,	
preferences	and	abilities.	They	might	equally	change	the	context	in	which	decisions	are	being	made	(for	
instance,	through	financial	rewards,	laws,	or	the	provision	of	energy-efficient	equipment)	and	as	a	result	
they	 could	 make	 energy	 saving	 behaviour	 relatively	 more	 attractive.	 For	 instance,	 households	 may	 save	
more	energy	by	properly	insulating	their	homes	than	by	lowering	thermostat	settings.	However,	the	use	of	
energy-efficient	 appliances	 does	 not	 necessarily	 result	 in	 reduction	 of	 the	 overall	 energy	 consumption,	
which	in	part	is	a	consequence	of	a	rebound	effect,	(Berkhout,	Muskens,	&	Velthuijsen,	2000).	To	avoid	a	
rebound	effect	might	require	intervention	strategies	that	provide	the	right	interplay	between	contextual	
factors	and	micro-level	factors,	though	the	literature	on	combined	intervention	strategies	appears	to	be	
scarce	 and	 there	 is	 apparently	 little	 evidence	 about	 the	 actual	 impact	 of	 such	 combined	 intervention
4.	Energy	use	and	intervention	strategies	
	
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strategies,	(Abrahamse	et	al.;	2005).	In	addition	to	this,	it	is	often	difficult	to	establish	the	contribution	of	
each	of	the	interventions	separately	and	the	volume	and	consistency	of	the	evaluations	that	are	currently	
available	 has	 been	 very	 poor,	 often	 vague	 and	 generic	 with	 very	 little	 empirical	 rigour	 presented,	
(Southerton	et	al.,	2011).	
4.1 	Energy	use,	Interventions	and	supportive	frameworks	
There	are	a	number	of	frameworks	within	the	environmental	field	that	attempt	to	support	intervention	
strategies	 to	 find	 the	 right	 interplay	 between	 the	 various	 existing	 factors.	 Frameworks	 from	 the	 field	 of	
behavioural	economics	approach	the	matter,	for	example,	by	putting	forward	a	set	of	external,	internal	and	
social	determinants,	so	as	to	understand	individual	behaviour.	The	overall	aim,	as	illustrated	in	Figure	4-1,	is	
to	provide	an	integrated	approach	to	change	behaviour	through	a	number	of	external,	internal	or	social	
factors,	 such	 as	 emotions	 or	 habits,	 which	 could	 change	 the	 balance	 of	 costs	 vs.	 benefits	 that	 is	 at	 the	
centre	 of	 the	 traditional	 economic	 perspective	 of	 understanding	 human	 behaviour,	 (Prendergrast	 et	 al.,	
2008).
4.	Energy	use	and	intervention	strategies	
	
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Figure	4-1:	Reducing	car	use:	Factors	affecting	behavioural	change,	(Prendergrast	et	al.	2008,	p.	104).
4.	Energy	use	and	intervention	strategies	
	
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From	a	behavioural	economic	perspective,	it	is	argued	that	individual	behaviours	are	influenced	by	a	much	
wider	range	of	factors	and	not	limited	to	one’s,	‘expected	net	benefits’.	Such	factors	include,	for	example,	
the	 impact	 of	 habits,	 emotions,	 cognitive	 capabilities,	 cultural	 attitudes	 and	 social	 norms.	 From	 an	
economic	perspective	all	of	such	factors	can	thus	impact	the	balance	of	an	individual’s	costs	vs.	benefit	
understanding	and	thus	impact	behaviour,	(Prendergrast	et	al.,	2008).	As	such,	informational	and	financial	
levers	alone	might	not	be	sufficient	to	explain	an	individual’s	behaviour	and	that	the	prevailing	rational	
model	 of	 behaviour	 is,	 in	 some	 circumstances,	 inappropriate	 once	 one	 considers	 how	 people	 make	
decisions,	(Prendergrast	et	al.,	2008).	
Another	framework	within	the	environmental	field	that	attempts	to	support	intervention	strategies	to	find	
the	 right	 interplay	 uses	 psychological	 interventions	 as	 a	 framework	 and	 tool	 to	 promote	 individual	
behavioural	change.	Focus	is	laid	on	changing	existing	perceptions,	knowledge,	attitudes,	norms	and	values	
under	the	assumption	that	this	then	would	result	in	behaviour	changing	accordingly,	(Abrahamse	et	al.,	
2005).	 Intervention	 can	 then	 address	 the	 community	 level	 and	 the	 social	 aspects	 of	 energy-related	
behaviour,	instead	of	the	individual	approach	that	has	been	dominating	the	area,	(Abrahamse	et	al.,	2005;	
Darby,	2006;	Heiskanen	et	al.,	2009;	Middlemiss,	2008).		
Another	framework	that	could	potentially	be	used	to	support	intervention	strategies	is	a	model	developed	
by	DEFRA	(UK	Department	for	Environment,	Food	and	Rural	Affairs),	under	the	UK’s	strategy	to	promote	
pro-environmental	 behaviours,	 as	 depicted	 in	 Figure	 4-2	 and	 which	 works	 alongside	 the	 four	 E	 factors,	
Enable,	Engage,	Exemplify	and	Encourage,	(DEFRA,	2008).
4.	Energy	use	and	intervention	strategies	
	
52	
	
Figure	4-2:	Diagrammatic	representation	of	the	4E’s	model,	(DEFRA,	2008,	p.	53).	
As	 can	 be	 seen	 from	 Figure	 4-2,	 promoting	 pro-environmental	 behaviour	 from	 the	 DEFRA	 4E	 Model	
framework	perspective	would	require	a	number	of	actions	to	result	in	habits	being	broken	and	new	more	
environmental	friendly	behaviours	adopted.	
A	further	framework	to	support	intervention	strategies	is	the	Mindspace	approach,	(Dolan,	2010),	which	
intends	 to	 take	 behavioural	science	to	the	very	heart	of	policy-making.	The	word,	Mindspace,	is	itself	a	
mnemonic	of	nine	non-coercive	influences	on	behaviour,	as	Figure	4-3	shows:	
	
Figure	4-3:	Mindspace’s	influences	on	behaviour,	(Dolan,	2010).	
From	 a	 Mindspace	 framework	 perspective,	 the	 approach	 seeks	 to	 influence	 behaviour	 by	 changing	 the	
context,	which	would	encourage	people	unconsciously	into	one	course	of	action,	rather	than	another.
4.	Energy	use	and	intervention	strategies	
	
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In	 summary,	 it	 can	 be	 clearly	 shown	 that	 there	 are	 a	 number	 of	 frameworks	 that	 attempt	 to	 support	
intervention	strategies	to	find	the	right	interplay	between	the	various	existing	factors	that	could	be	used	to	
encourage	the	adoption	of	more	energy	efficient	behaviours.	Each	framework	shows	a	slight	variation	in	
terms	of	existing	factors	and	approach.	
4.1.1 	Potential	intervention	layers	
As	much	as	the	right	interplay	between	the	contextual	factors	and	micro-level	factors	influence	energy	use	
at	home,	so	do	a	diversity	of	determinants,	motivations	and	barriers.	They	all	are	considered	influential	to	
energy	 use	 at	 home	 and	 thus	 might	 be	 taken	 into	 account	 for	 any	 intervention	 attempts.	 Behavioural	
change	interventions	tend	to	address	at	least	one	of	the	contexts	in	which	behaviour	might	be	changed,	
individual,	social,	or	contextual/material	spheres,	(Southerton	et	al.,	2011),	as	illustrated	in	Figure	4-4.	
	
Figure	4-4:	The	relation	between	material,	social	and	individual	contexts,	adapted	from	Southerton	et	al.	(2011).	
Figure	 4-4	 illustrates	 that	 influencing	 the	 individual	 sphere	 might	 require	 interventions	 to	 focus	 on	 the	
individual	attitudes	so	as	to	change	behaviours	and	choices.	Within	the	social	sphere,	such	interventions	
will	 address	 social	 norms,	 cultural	 conventions	 and	 shared	 understanding	 of	 practices.	 In	 the	
contextual/material	 sphere,	 intervention	 might	 refer	 to	 the	 objects,	 technologies,	 and	 infrastructures,	
which	can	enable	or	constrain	the	adoption	of	new	behaviours,	(Southerton	et	al.,	2011).	Following	from	
this,	Figure	4-5,	builds	from	Barenergy	(2011)	and	summarizes	what	could	motivate,	enable	and	reinforce
4.	Energy	use	and	intervention	strategies	
	
54	
individual	 behavioural	 change	 in	 relation	 to	 the	 barriers,	 that	 literature	 indicates	 exist,	 that	 need	 to	 be	
addressed	and	finally,	the	type	of	interventions	that	could	be	used	in	order	to	promote	change.	
	
Figure	4-5:	The	relation	between	energy	use	determinants,	motivations,	barriers	to	change	and	types	of	intervention,	
adapted	from,	(Barenergy,	2011).	
As	 Figure	 4-5	 illustrates,	 there	 might	 be	 two	 different	 layers	 of	 intervention.	 One	 that	 addresses	 the	
external/macro	factors,	such	as	the	need	of	an	adequate	legal	framework,	or	the	deployment	of	financial	
instruments,	that	could	promote	individual	change	and	one	that	promotes	internal	change	by	influencing	
values,	 beliefs	 or	 perceptions.	 Comfort,	 convenience,	 individual	 willingness,	 motivation,	 opportunity	 and	
ability	are	all	identified	determinants	that	influence	energy	use	at	home	and	as	have	been	detailed	through	
Chapters	two	and	three.	Thus	there	appear	to	be	a	number	of	intervention	layers	(Fig	4-4)	and	factors	(Fig	
4-5),	though	the	literature	appears	undecided	as	to	which	could	encourage	lasting	change.	
4.2 	Behavioural	change,	communication	and	persuasion	
Persuasion	can	influence	others	by	modifying	their	beliefs,	values,	or	attitudes,	(Simons,	1976,	p.	21)	and	
ultimately	 their	 behaviour,	 (Jackson,	 2005;	 Martiskainen,	 2007).	 Persuasion	 is	 often	 based	 on	 three	
principles;	(1),	the	credibility	of	the	sender	(2),	the	persuasiveness	of	the	argument/message	and	(3),	the
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responsiveness	of	the	audience,	(O’Keefe,	1990).	Persuading	people	to	change	can	be	particularly	difficult	in	
a	message-dense	environment	and	effective	persuasion	requires	a	number	of	principles	to	be	met	such	as,	
understanding	the	target	audience,	using	emotional	and	imaginative	appeals,	immediacy	and	directness,	
commitments/loyalty	 schemes	 and	 the	 use	 of	 ‘retrieval	 cues’	 to	 catalyse	 the	 new	 behaviour,	 (Jackson,	
2005).	 There	 are	 a	 number	 of	 persuasion	 theories	 and	 approaches	 that	 might	 be	 applied	 to	 promote	
behavioural	change.		
The	cognitive	dissonance	theory,	(Festinger,	1957)	assumes,	for	example,	that	people	prefer	congruency,	
i.e.	people	are	motivated	to	avoid	internal	inconsistency	(dissonance),	between	values,	beliefs,	attitudes	
and	 behaviour.	 These	 feelings	 of	 discomfort	 might	 arise	 from	 conflicting	 attitudes	 or	 values,	 but	 might	
equally	be	invoked	by	discrepancies	between	an	attitude,	e.g.	about	the	self,	and	behaviour	highlighting	the	
desire	 for	 attitude-behaviour	 consistency,	 (Jackson,	 2005).	 The	 theory	 suggests	 that	 once	 engaging	 in	 a	
behaviour	 that	 opposes	 attitudes,	 people	 experience	 distress	 and	 an	 uncomfortable	 psychological	 state	
resulting	 from	 the	 awareness	 of	 holding	 conflicting	 beliefs,	 or	 acting	 inconsistently	 with	 one’s	 attitudes.	
Depending	on	the	importance	of	the	issue	and	the	degree	of	discomfort,	people	then	will	be	persuaded	to	
change	beliefs,	attitudes	or	behaviours	in	order	to	reduce	inconsistencies	in	the	cognitive	information	that	
they	 hold	 about	 themselves,	 their	 behaviour,	 or	 their	 environment,	 (Brehm	 &	 Kassin,	 1996;	 Dainton	 &	
Zelley,	2005).	In	accordance	to	Brehm	and	Kassin	(1996),	people	tend	to	adopt	one	of	three	strategies	to	
reduce	dissonance:	(1),	changing	their	attitude	to	justify	their	behaviour,	particularly	for	long-term	habits	
where	 it	 is	 suggested	 that	 people	 readjust	 their	 long-term	 goals	 rather	 than,	 “changing	 the	 habit	 of	 a	
lifetime”,	(Jackson,	2005,	pp.	114-115).	An	example	of	this	would	be	the	London	congestion	charge,	where	
public	opinion	was	opposed	before	it	was	introduced,	but	seems	to	have	changed	once	the	charge	was	
introduced,	(Darnton,	2008;	Knott	et	al.,	2008).	(2),	Claiming,	or	perceiving,	to	have	little	or	no	choice	of	
action,	i.e.	reducing	dissonance	by	under-reporting	knowledge	about	the	impact	of	particular	behaviours,	
(Darnton,	2008),	For	example,	under-report	knowledge	on	how	to	reduce	energy	use	in	order	to	reduce	the	
unavoidable	contradiction	in	responses	to	questions	about	personal	energy	use.	This	could	be	one	of	the	
reasons	 for	 decreasing	 levels	 of	 reported	 knowledge	 once	 moving	 from	 bigger	 issues,	 such	 as	 climate	
change,	towards	more	specific	behaviours,	such	as	energy	saving	at	home.	(3)	By	denying	any	inconsistency,	
i.e.	 denying	 personal	 responsibility	 for	 tackling	 the	 problem,	 or	 by	 ‘over-claiming’	 the	 involvement	 in,
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“Issues	which	people	think	they	ought	to	be	seen	to	be	involved	in”,	(Darnton,	2008,	p.	12).	With	regards	to	
denial	of	inconsistencies,	the	literature	provides	three	equally	different	ways	on	how	this	might	happen.	
Firstly,	 people	 might	 underestimate	 individual	 energy	 use	 as	 well	 as	 its	 contribution	 to	 environmental	
problems.	 Secondly,	 by	 overestimating	 the	 prevalence	 of	 non-conservation	 as	 a	 habit	 shared	 by	 other	
people,	suggesting	this	to	be	a	normal,	societal	behaviour.	Thirdly,	by	over-claiming	the	frequency	of	pro-
environmental	activities,	such	as	recycling,	as	a	way	to	support	the	feeling	of	personal	contribution	and	
reinforcing	the	perception	of	already	doing	everything	they	can,	(Cialdini	et	al.,	1990;	van	der	Pligt,	1985.)		
An	alternative	persuasion	theory	that	might	be	applied	is,	Higgins’s	(1987)	Self	Discrepancy	Theory,	that	
assumes	 that	 the	 individual	 self-concept	 is	 derived	 partly,	 from	 ones’	 own	 perspective	 of	 ‘myself’	 and	
partly,	from	‘my’	perceptions	of	others’	perspectives	of	me.	The	theory	distinguishes	between	six	distinct	
types	of	self-concept:	actual-own,	actual-other,	ideal-own,	ideal-other,	ought-own	and	ought-other,	with	
discrepancies	giving	rise	to	different	types	of	emotional	response.	For	example,	discrepancy	between	‘my’	
actual	self-concept	and	‘my’	ideal	self-concept	is	likely	to	give	rise	to	dejection-related	emotions,	such	as	
disappointment	and	dissatisfaction.	Discrepancies	between	‘my’	actual	self-concept	and	the	ideal	concept	
others	have	of	me,	on	the	other	hand,	are	most	likely	to	give	rise	to	feelings	of	shame	or	embarrassment.	
Incongruities	between	‘my’	actual	self-concept	and	‘my’	ought	self-concept	are	likely	to	give	rise	to	feelings	
of	guilt.	
Social	 judgment	 theory,	(C.	W.	Sherif,	Sherif,	&	Nebergall,	1965;	M.	Sherif	&	Hovland,	1961),	is	 another	
persuasion	theory	that	might	be	used	and	that	assumes	that	people	make	evaluations,	so	called	judgments,	
about	the	content	of	messages	based	on	their	anchors	on	a	particular	topic.	When	the	topic	is	one	that	has	
personal	significance	to	the	individual,	it	is	considered	to	be	central	to	their	sense	of	self,	hence,	they	are	
ego-involved,	(Dainton	&	Zelley,	2005).	The	theory	suggests	that	each	person’s	attitudes	can	be	placed	into	
one	of	three	categories,	with	the	individual	reaction	to	a	persuasive	message	depending	on	the	position	on	
the	topic,	(M.	Sherif	&	Hovland,	1961):	(1),	the	latitude	of	acceptance,	includes	all	those	ideas	that	people	
find	acceptable	(2),	the	latitude	of	rejection,	includes	all	those	ideas	that	people	find	unacceptable	and	(3),	
the	latitude	of	non-commitment,	includes	those	ideas	for	which	people	have	no	opinion.	Social	judgment	
theory	proposes	that	persuaders	must	carefully	consider	the	pre-existing	attitudes	of	an	audience	before
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designing	the	message.	According	to	the	theory,	three	scenarios	can	take	place:	(1),	sending	a	message	that	
falls	into	people’s	latitude	of	rejection	might	lead	to	unsuccessful,	persuasive	effort,		(2),	sending	a	message	
aimed	at	people’s	latitude	of	acceptance	might	only	lead	to	reinforcement	of	what	people	already	believe,	
rather	than	persuasion,	or	(3),	sending	a	message	targeted	to	people’s	latitude	of	non-commitment,	or	the	
edges	of	it,	would	be	true	persuasion,	(Dainton	&	Zelley,	2005;	Miller,	2002).	
A	further	persuasion	theory	that	could	be	applied,	is	the	elaboration	likelihood	model,	(Petty	&	Cacioppo,	
1986),	that	predicts	that	if	listeners	are	motivated	and	able	to	consider	an	elaborated	message,	persuaders	
should	 rely	 on	 strong,	 factually	 based	 arguments	 and	 that	 arguments	 can	 backfire	 if	 they	 are	 weak,	 or	
poorly	 presented,	 (Dainton	 &	 Zelley,	 2005).	 Conversely,	 persuaders	 should	 focus	 on	 emotionally	 based	
peripheral	 messages	 if	 receivers	 cannot,	 or	 will	 not,	 consider	 an	 elaborated	 message,	 even	 though	
recognizing	that	using	a	peripheral	route	is	expected	to	guarantee	no	long-term	change,	but	rather	minimal	
and	transitory	effects,	(Petty	&	Cacioppo,	1986).	
As	can	be	seen,	there	are	numerous	persuasion	theories	and	while	each	of	them	varies	in	their	respective	
approach,	 they	 all	 might	 be	 applied	 to	 promote	 behavioural	 change	 and	 as	 will	 be	 further	 examined	 in	
Chapter	8,	once	it	comes	to	perceived	requirements	(RQ3a)	and	individual	perceptions	on	the	effectiveness	
of	intervention	strategies	(RQ3b).		
4.2.1 	Persuasion	and	communication	
Persuasion	is	often	associated	with	communication	and	behaviour	change	intervention.	Literature	suggests	
that	 unpopular	 messages,	 such	 as	 the	 need	 to	 change	 lifestyles	 and	 to	 reduce	 consumption,	 may	 be	
rejected,	or	ignored,	to	avoid	confronting	the	implications	for	appreciated	behaviours,	(Feinberg	&	Willer.,	
2010;	Upham	et	al.,	2009,	van	der	Pligt,	1985).	Thus	there	might	be	the	need	for	creating	a	new	balance	by	
changing	 individual	 attitudes	 rather	 than	 behaviour,	 (Gass	 &	 Seiter.,	 2003).	 As	 such	 attempts	 to	 shame	
individuals	into	adopting	pro-environmental	behaviours	can	be	ineffective	in	changing	behaviours,	(O’Keefe,	
2002);	any	type	of	persuasion	attempt	should	be	framed	in	a	way	to	build	up	narratives	to	which	individuals	
can	connect.	Altogether,	this	implies	that	any	type	of	message	that	refers	to	potential	solutions	should	be
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delivered	in	a	positive,	and	not	confrontational	frame,	therefore	encouraging	individuals	to	believe	in	their	
ability	to	contribute	to	what	they	perceive	as	a	positive	change.	
4.2.2 	Mental	models	and	communication	
Individuals	 use	 their	 knowledge	 and	 beliefs	 to	 help	 them	 interpret	 new	 information	 in	 order	 to	 reach	
conclusions.	A	mental	model	represents	a	person’s	thought	process	for	how	something	works	and	serves	as	
the	framework	to	fit	new	information,	(Morgan,	Fischhoff,	Bostrom,	&	Atman,	2002).	Mental	models	are	
often	based	on	incomplete	facts,	past	experiences	and	even	intuitive	perceptions,	that	help	shape	actions	
and	 behaviour,	 influence	 what	 people	 pay	 attention	 to	 and	 define	 how	 people	 approach	 and	 solve	
problems,	(Carey,	1986).	But,	by	working	as	a	framework,	sometimes	a	mental	model	may	also	work	as	a	
filter,	resulting	in	only	selective	knowledge	being	considered,	with	people	seeking	out,	or	absorbing,	the	
information	 that	 only	 matches	 their	 mental	 model.	 Here,	 they	 might	 be	 confirming	 what	 they	 already	
believe	about	an	issue,	which	then	could	pose	a	potential	challenge	for	communication	aiming	at	promoting	
more	energy	efficient	behaviours.	This	situation	is	known	within	the	literature	as	a	confirmation	bias,	as	
people	look	for	information	that	is	consistent	with	what	they	already	think,	want,	or	feel,	leading	them	to	
avoid,	dismiss,	or	forget	information	that	requires	them	to	change	their	position	and,	quite	possibly,	their	
behaviour,	(Shome	&	Marx,	2009).	It	might	be	thus	that	once	people	say,	“I	can’t”,	that	it	simply	means,	“I	
don’t	want	to”.	Thus	an	important	criterion	for	effective	communication	is	to	know	the	audience,	what	they	
understand	and	misunderstand	about	the	issue,	how	they	perceive	a	threat	to	their	current	and	intended	
behaviours,	 their	 values,	 beliefs	 and	 policy	 preferences,	 or	 their	 barriers	 to	 change	 and	 underlying	
motivations.	All	of	these	could	either	constrain,	or	inspire,	further	engagement	with	solutions,	(Maibach	et	
al.,	2009).	Practitioners	thus	need	to	discover	what	misconceptions	the	audience	may	have	in	their	mental	
models,	 so	 that	 information	 can	 be	 actively	 communicated	 with	 appropriate	 language,	 metaphor,	 and	
analogy,	 i.e.	 combined	 with	 narrative	 storytelling,	 made	 vivid	 through	 visual	 imagery	 and	 experiential	
scenarios,	 balanced	 with	 scientific	 information	 and	 delivered	 by	 trusted	 messengers	 in	 group	 settings,	
(Shome	&	Marx,	2009).	Framing	is	thus	perceived	as	the	setting	of	an	issue	within	an	appropriate	context	to	
achieve	a	desired	interpretation,	or	perspective.	In	addition,	to	frame	the	message,	practitioners	also	need	
the	specifics	of	the	target	audience	and	their	segmentation,	in	order	to	prepare	frames	in	advance	to	fit	
with	the	audience	mental	models,	(Shome	&	Marx,	2009).	To	be	successful,	messages	might	also	consider
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individuals’	goals	and	whether	their	goal	is	to	make	something	good	happening,	or	preventing	something	
bad	from	happening,	(Shome	&	Marx,	2009).	
4.2.3 	Behavioural	change,	and	relevant	and	supportive	communication		
Humans	hold	a	limited	capacity	for	worrying;	they	have	a	finite	pool	of	worry,	(Linville	&	Fischer,	1991),	
therefore	tending	to	view	near-term	threats	as	more	relevant	and	of	greater	urgency	than	caring	about	
future	problems,	(Slovic,	2000;	Slovic	et	al.,	2004;	Weber,	2006).	People	thus	tend	not	to	immediately	react	
to	 threats	 that	 may	 manifest	 themselves	 in	 the	 distant	 future,	 but	 rather	 look	 for	 balancing	 long-range	
worries	with	the	demands	of	more	immediate	concerns,	(Chaiken	&	Trope,	1999;	Marx	et	al.,	2007).	The	
literature	 suggests	 this	 to	 be	 one	 of	 the	 barriers	 to	 motivate	 people	 into	 taking	 action	 to	 prevent	
environmental	problems,	(Shome	&	Marx,	2009).	In	addition	to	this,	individuals	have	a	natural	tendency	to	
avoid	 losses,	 rather	 than	 to	 seek	 gains,	 (Kahneman	 &	 Tversky,	 1979).	 Once	 a,	 ‘gain	 vs.	 loss’,	 frame	 is	
combined	with	a,	‘now	vs.	future’,	frame,	people	discount	future	gains	more	than	future	losses,	(Thaler,	
1981).	For	example,	people	may	be	more	likely	to	adopt	environmentally	friendly	behaviours	if	they	believe	
their	way	of	life	is	threatened	and	that	inaction	will	result	in	even	greater	threats,	thus	addressing	people’s	
desire	to	avoid	future	losses	rather	than	realizing	future	gains.	They	might	be	less	likely	to	adopt	these	
measures	 if	 they	 focus	 on	 the	 current	 situation,	 which	 they	 see	 as	 acceptable	 and	 discount	 future	
improvements	of	it.	Thus	any	type	of	communications	should	be	relevant	and	supportive.	Shome	&	Marx	
(2009),	 provide	 an	 example	 for	 such	 relevant	 and	 supportive	 communication	 by	 promoting	 energy	
efficiency	appliances	as	helping	the	homeowners	to	avoid	losing	money	on	higher	energy	bills	in	the	future,	
instead	of	helping	them	save	money	in	the	future.	
4.3 	Structural	interventions	
As	 can	 be	 seen	 in	 Figure	 4-5	 (p.50),	 there	 are	 a	 number	 of	 intervention	 types	 that	 can	 be	 grouped	 in	
between	 structural	 and	 psychological	 interventions,	 (Poortinga	 et	 al.,	 2004;	 Steg,	 2003).	 Structural	
interventions	 aimed,	 for	 example,	 at	 changing	 the	 (social),	 context	 in	 which	 behavioural	 decisions	 take	
place	 (Fig.	 4-5),	 are	 based	 on	 the	 belief	 that	 by	 altering	 the	 conditions	 in	 which	 behaviour	 takes	 place,
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behaviour	 will	 change	 accordingly	 (Fig.	 4-5).	 Structural	 interventions	 include,	 for	 example,	 financial-
economic	measures,	physical/technical	alternatives,	and	legal	regulation,	(Steg,	2003).		
4.3.1 	Financial-economic	interventions	
Financial-economic	 measures	 hold	 the	 potential	 to	 promote	 energy	 saving	 by	 making	 energy-intensive	
behaviours	relatively	more	expensive	and	environmentally-friendly	alternatives	relatively	less	expensive.	To	
illustrate,	 increasing	 the	 costs	 of	 energy	 use,	 by	 means	 of	 a	 tax	 on	 gas	 and	 electricity,	 may	 induce	
households	to	reduce	their	energy	use,	(Streimikiene	&	Ciegis,	2010).	Furthermore,	increasing	the	prices	of	
products	that	require	much	energy	may	encourage	households	to	choose	less	energy-intensive	alternatives.	
Nevertheless,	these	kinds	of	measures	only	tend	to	be	effective	if	consumers	take	the	financial	cost	into	
account	when	making	such	choices.		
4.3.2 	Physical/technical	interventions	
Physical/technical	alternatives	involve	changes	to	already	existing	infrastructure	and	equipment,	such	as	
the	 introduction	 of	 energy-efficient	 appliances.	 There	 is	 some	 overall	 agreement	 that	 efficiency	
improvements	are	necessary	for	sustainable	development,	but	nevertheless	technological	innovations	are	
perceived	as	a	partial	solution,	as	the	effectiveness	of	technological	measures	requires	the	adoption	of	new	
technology,	as	well	as	the	knowledge	of	how	to	use	such	technologies	efficiently,	(Abrahamse,	2007;	Steg,	
2003).	In	addition	to	this	a	possible	rebound	effect,	as	identified	by	Khazzoom	(1980),	may	also	occur,	in	
that	consumers	may	increase	the	use	of	efficient	appliances,	thus	counterbalancing	initial	efficiency	gains.		
4.3.3 	Legal	regulation	
Also	there	is	legal	regulation	as	entailed	by	the	introduction	of	legislation	by	the	government,	such	as	speed	
limits	for	cars	in	order	to	reduce	carbon	dioxide	emissions.	Often	this	form	of	measures	is	associated	with	
some	form	of	punishment	to	those	whose	behaviour	deviates	from	the	regulations	and	is	based	on	the	
assumption	that	these	rules	will	eventually	become	internalized.	Regulatory	measures	may	be	an	effective	
strategy	for	behavioural	change,	provided	the	monitoring	and	enforcement	system	works	properly.
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4.4 	Psychological	interventions		
In	 contrast	 to	 structural	 interventions,	 psychological	 interventions	 aim	 to	 change	 existing	 perceptions,	
knowledge,	 attitudes,	 norms	 and	 values	 (i.e.	 individual-level	 variables),	 so	 that	 behaviour	 will	 change	
accordingly,	 (Southerton	 et	 al.,	 2011).	 	 A	 recent	 review	 of	 the	 potential	 of	 structural	 and	 psychological	
intervention	strategies	has	proved	that	the	most	promising	approaches	involved	energy	audits,	community	
based	interventions	and	the	combination	of	more	than	one	type	of	intervention,	and	producing	savings	of	
between	 2	 and	 20	 percent,	 depending	 on	 the	 type	 of	 intervention,	 (EEA,	 2013).	 There	 are	 a	 number	 of	
models	 that	 attempt	 to	 support	 psychological	 intervention,	 such	 as	 the	 three	 term	 contingency	 ABC
11
	
(Antecedent-Behaviour-Consequence),	 model	 of	 behavioural	 change,	 (Geller,	 2002),	 that	 assumes	 that	
behaviours	 are	 directed	 by	 antecedent	 stimuli	 that	 preceded	 them	 and	 that	 state	 the	 availability	 of	 a	
positive,	or	negative,	consequence,	(Dwyer,	Leeming,	Cobern,	Porter,	&	Jackson,	1993;	Geller	et	al.,	1990;	
Lehman	 &	 Geller,	 2004).	 Antecedent-Behaviour	 interventions	 attempt	 to	 influence	 one	 or	 more	
determinants	 prior	 to	 the	 performance	 of	 the	 determinant	 behaviour.	 Examples	 of	 antecedent	
interventions	such	as	commitment,	goal	setting,	modelling	and	information,	(Abrahamse	et	al.,	2005)	aim	at	
influencing	underlying	behavioural	determinants	(e.g.	knowledge).	On	the	other	side	of	the	ABC	model	are	
Behaviour-Consequence	interventions,	which	are	based	on	the	assumption	that	once	positive	or	negative	
consequences	 are	 attached	 to	 certain	 behaviour,	 this	 will	 subsequently	 lead	 to	 an	 alteration	 of	 this	
behaviour,	 (Geller,	 2002).	 Within	 the	 environmental	 context	 this	 implies,	 for	 example,	 that	 pro-
environmental	 behaviour	 becomes	 a	 more	 attractive	 alternative,	 once	 positive	 consequences,	 such	 as	
monetary	 incentives,	 are	 attached	 to	 it.	 Feedback	 and	 rewards	 are	 another	 possible	 Behaviour-
Consequence	strategy.	For	instance,	once	households	receive	feedback	about	their	efforts	to	reduce	energy	
use,	they	may,	as	a	result	of	the	positive	consequences	attached	to	their	behaviour,	be	motivated	to	further	
conserve	energy	since	they	might	have	become	knowledgeable,	(Geller,	2002).	Savings	have	been	shown	in	
the	region	of	5	–	15	percent	for	direct	feedback	and	0–	10	percent	for	indirect	feedback,	(Darby,	2006).	
Recent	 research	 on	 smart	 metering	 and	 householder	 engagement	 has,	 however,	 equally	 found	 that	
feedback	alone	is	not	enough	to	interest	occupants,	(Darby,	2010).	
																																																																				
11
	Not	to	be	confused	with	the	ABC	behavioural	change	model	developed	by	Stern	et	al	(1995)
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Following,	a	number	of	such	psychological	intervention	approaches	will	be	discussed.	
4.4.1 	Information	provision	
Providing	 information	 aims	 to	 increasing	 knowledge	 regarding	 energy	 use,	 which	 in	 turn	 is	 expected	 to	
result	in	the	adoption	of	more	energy	efficient	behaviour,	(Geller,	2002).	This	assumption	of	information	
provision	as	a	predecessor	of	behaviour	can	be	grounded	in	the	Knowledge	Deficit	Theory	(KDT),	a	theory	
that	advocates	for	a	causal	relationship	between	knowledge	and	behaviour,	(Schultz,	2002).	KDT’s	primary	
assumption	is	that	people	want	to	help	themselves	and	the	environment,	but	they	lack	information	about	
how	and/or	why	they	should	make	changes	to	their	behaviour.	As	such,	the	provision	of	information	about	
how,	or	why,	one	should	act	would	help	overcoming	inaction	and	lead	to	the	desired	behaviour.	From	the	
literature	 it	 is,	 however,	 not	 entirely	 clear	 whether	 this	 cause-effect	 is	 indeed	 taking	 place	 and	 that	
information	regarding	energy	saving	measures	is	leading	to	a	reduction	of	energy	use.	This	cause-effect	
relation	might	be,	for	example,	negatively	impacted	by	limited	time	and	capacity	to	process	all	the	available	
information,	or	because	insight	alone	does	not	necessarily	change	behaviour,	or	since	the	subject	of	energy	
use	 might	 be	 too	 complex	 to	 be	 changed	 by	 single,	 stand-alone	 interventions,	 such	 as	 information	 and	
feedback	provision.		
Information	provision,	as	a	way	to	increase	individual	awareness	of	problems	related	to	energy	use,	as	well	
as	to	increase	the	knowledge	about	possible	alternatives,	has	been	widely	used	for	promoting	energy	saving	
and	conservation	behaviours,	(Abrahamse	et	al.,	2005).	In	the	spheres	of	policy	and	the	energy	research	
community,	the	information	deficit	model	tends	to	dominate,	(Janda,	2011).	The	provision	of	information,	
or	feedback,	is	perceived	as	a	way	of	‘teaching’	people	the	required	energy	management	skills	and	in	giving	
people	 a	 sense	 of	 their	 ability	 to	 control	 energy	 use,	 (Chatterton,	 2011).	 Information	 provision	 covers	 a	
large	 spectrum	 of	 interventions,	 mass	 media	 campaigns,	 information	 and	 training	 centres,	 technical	
manuals	and	brochures,	labelling	and	energy	audits,	and	can	be	used	for	providing	detailed	information	to	
various	actors,	consumers,	equipment	operators/technicians,	managers	of	building	complexes,	engineers,	
architects	and	decision	makers,	(BPIE,	2011).	Individuals	are	often	presented	with	a	number	of	suggested
4.	Energy	use	and	intervention	strategies	
	
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pro-environmental	 behaviours	 in	 the	 form	 of,	 ‘To	 Do’
12
	 lists,	 which	 are	 unranked	 lists	 of	 recommended	
actions	which	aim	to	provide	some	guidance	and	help	to	individuals	having	an	understanding	of	the	type	of	
pro-environmental	behaviours	they	could	adopt,	(Gardner	&	Stern,	2008).	It	has	been	observed	however,	
that	such	guidance	and	‘To-do’	lists	could	equally	lead	to	individuals	deciding	to	take	no	action	at	all,	or	to	
only	 carry	 out	 one	 or	 two	 actions,	 or	 perhaps,	 to	 engage	 with	 those	 actions	 that	 are	 the	 easiest	 to	
remember	and	perform,	regardless	of	the	environmental	impact	those	actions	might	have,	(Barr	&	Gilg,	
2006;	Darnton,	2008;	Gardner	&	Stern,	2008).	
Information	campaigns	are	also	found	to	be	cost	efficient	and	an	easy	to	implement	means	to	overcome	
information	barriers,	though	the	literature	equally	found	that	information	campaigns	often	have	little,	or	
no,	impact	on	promoting	behavioural	change	and	thus	can	be	expensive	in	relation	to	their	effectiveness,	
(McKenzie-Mohr,	 2000;	 Southerton	 et	 al.,	 2011).	 Evidence	 suggests	 that	 information	 alone	 is	 seldom	
sufficient	to	promote	change,	(Abrahamse	et	al.,	2005;	Geller,	2002;	Staats	et	al.,	1996).	Yet,	in	cases	where	
lack	 of	 knowledge	 has	 been	 identified	 as	 a	 barrier	 to	 participation,	 information	 dissemination	 seems	 to	
motivate	changes	in	behaviour,	(Geller,	2002).	Nevertheless,	research	also	found	that	people	often	possess	
the	knowledge	required	to	engage	in	modifying	behaviour,	but	they	lack	the	motivation	for	doing	so,	which	
indicates	the	existence	of	an,	‘information-behaviour	gap’,	between	the	held	information	and	behaviour,		
(Geller,	2002;	Jackson,	2005;	Prochaska,	DiClemente,	&	Norcross,	1992;	Schultz,	2002;	Southerton	et	al.,	
2011;	Stern,	1999).	One	example	for	such	an	information-behaviour	gap	is	Al	Gore’s	film,	‘An	Inconvenient	
Truth,’	 that	 emphasized	 the	 seriousness	 of	 the	 global	 climate	 crisis,	 argues	 that	 it	 could	 be	 solved	 with	
present	 and	 foreseeable	 technology,	 and	 concludes	 that	 all	 citizens	 could	 play	 a	 meaningful	 role	 in	 the	
solution,	thus	creating	a	sense	of	awareness	regarding	the	need	for	change	for	the	better.	Research	found	
that	 watching	 the	 movie	 increased	 knowledge	 about	 the	 causes	 of	 global	 warming,	 concern	 for	 the	
environment	and	willingness	to	reduce	greenhouse	gases,	but	this	willingness	didn’t	necessarily	translate	
into	action,	(Gardner	&	Stern,	2008;	Nolan,	2010).	A	review	of	intervention	studies	on	household	energy	
																																																																				
12
	To	Do	lists	come	in	a	number	of	formats:		
‘20	things	you	can	do’	http://www.ecomall.com/greenshopping/20things.htm	
‘101	Ways	To	Heal	The	Earth’	http://www.context.org/ICLIB/IC22/Guide.htm	
‘100	Ways	to	Save	The	Environment	http://www.seql.org/100ways.cfm
4.	Energy	use	and	intervention	strategies	
	
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conservation	carried	out	by	Abrahamse	et	al.	(2005),	provided	some	further	evidence	for	the	existence	of	
an	 information-behaviour	 gap.	 They	 found	 that	 workshops,	 mass	 media	 campaigns	 and	 even	 targeted	
information	provision	in	general	led	to	higher	levels	of	concern	about	the	energy	crisis,	to	an	increased	level	
of	 knowledge	 about	 energy	 conservation,	 of	 (self-reported),	 conservation	 behaviours	 and	 to	 stronger	
intentions	to	adopt	energy-saving	measures.	However,	even	though	information	might	have	influenced	the	
underlying	 determinants	 of	 energy	 use,	 Abrahamse	 et	 al.	 (2005),	 found	 no	 clear	 evidence	 that	 this	 also	
resulted	in	any	reduction	in	energy	use.	
The	 literature	 does	 provide,	 however,	 some	 evidence	 that	 information	 provision	 could	 support	 the	
adoption	of	more	energy	efficient	behaviours.	Information	provision	might	support	the	adoption	of	energy	
efficient	behaviours	when	used	in	combination	with	other	type	of	intervention,	such	as	feedback	provision,	
or	auditing	and	personalised	advice,	(Abrahamse	et	al.,	2005).	Equally,	information	strategies	that	made	use	
of,	 for	 example,	 face-to-face	 interventions,	 which	 used	 feedback	 mechanisms	 such	 as	 monitoring	
equipment	(water	or	energy),	or	that	included	individual	pledges	to	a	long	term	commitment	to	reduce	
consumption,	seemed	to	support	the	adoption	of	energy	efficient	behaviours,	(Southerton	et	al.,	2011).	For	
example,	 Staats,	 Leeuwen,	 and	 Wit	 (2000),	 found	 that	 office	 workers	 improved	 their	 energy	 efficient	
behaviours,	 such	 as	 keeping	 thermostat	 settings	 consistent	 and	 removing	 objects	 from	 heating	 grates,	
immediately	after	an	informational	brochure	was	handed	out	to	them.	Subsequently,	other	intervention	
components,	 such	 as	 poster	 prompts	 and	 feedback,	 were	 added	 to	 maintain	 these	 energy	 efficient	
behaviours.	The	results	of	these	subsequent	intervention	components	demonstrated	that	energy	efficient	
behaviours	benefited	from	the	combination	of	different	strategies.	Secondly,	information	provision	might	
also	 be	 more	 effective	 if	 such	 information-based	 interventions	 are	 tailored	 to	 fit	 specific	 situations,	
(Abrahamse	et	al.,	2005).	Tailored	information	is	highly	personalized	and	specific	information.	An	advantage	
of	this	approach	is	that	people,	instead	of	getting	an	overload	of	general	information,	which	may	not	apply	
to	their	situation,	receive	tailored	information	only.	Examples	of	tailored	information	are	energy	audits,	i.e.	
a	home	visit	by	an	auditor	who	supplies	a	range	of	energy-saving	options	based	on	their	current	situation.	
For	instance,	auditors	may	advise	a	household	to	apply	insulation	and/or	to	lower	thermostat	settings	as	
well	as	a	complementary	set	of	curtailment	behaviours,	(Abrahamse,	Steg,	Vlek,	&	Rotehengatter,	2007).	
Previous	research	shows	that	home	energy	audits	(mainly	focusing	on	heating	and	air	conditioning),	might
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be	a	very	efficient	intervention	measure	to	increase	energy	savings	in	households,	(Abrahamse,	2003,	2007;	
Leiserowitz	et	al.,	2009).	Thirdly,	tailored	information,	targeted	at	an	intended	population	segment,	also	
appeared	to	support	the	adoption	of	energy	efficient	behaviours,	(Leiserowitz	et	al.,	2009;	Southerton	et	
al.,	2011).	Successful	information	campaigns	seem	to	use	practices	that	are	nowadays	commonly	accepted	
as	 good	 campaign	 design	 practices:	 simple,	 clear	 messages,	 repeated	 often	 through	 a	 variety	 of	
interpersonal	and	media	channels,	by	a	variety	of	trusted	sources,	(Streimikiene,	2012).		
4.4.2 	Commitment	and	goal	setting	
Commitment	strategies	involve	asking	participants	to	make	a	verbal,	or	written,	commitment	to	perform	a	
desired	behaviour,	such	as	to	save	energy,	which	is	often	linked	to	a	specific	goal	or	reference	point,	for	
instance,	 to	 reduce	 energy	 use	 by	 X	 percent,	 (Abrahamse	 et	 al.,	 2005).	 Goal	 setting	 is	 often	 used	 in	
combination	 with	 other	 interventions,	 such	 as	 feedback	 (to	 indicate	 how	 households	 are	 performing	 in	
relation	to	the	goal),	or	as	part	of	a	commitment	to	conserve	a	certain	amount	of	energy.	Cialdini	(2001),	
argued	that	once	people	have	made	a	commitment,	they	are	more	likely	to	perform	their	target	behaviour,	
especially,	if	the	commitment	is	active,	public,	and	perceived	as	voluntary.	Commitment	strategies	might	
also	 draw	 on	 the	 social	 norm	 of	 consistency,	 which	 creates	 pressure	 to	 be	 internally	 and	 externally	
consistent,	depending	on	whether	the	pledge	was	to	oneself,	or	public,	(Cialdini,	2001).	Pledges	to	oneself	
may	activate	a	personal	norm,	meaning	a	moral	obligation,	with	public	pledges	activating	social	norms,	the	
expectation	of	others	to	pursue	the	behaviour.	Commitment	strategies	are	often	seen	as	a	way	to	use	the	
‘foot-in-the-door’	 technique	 that	 assumes	 that	 compliance	 to	 a	 first	 (smaller),	 request	 will	 result	 in	
compliance	to	a	subsequent	(bigger),	request,	(Abrahamse	et	al.,	2005).	The	efficacy	of	commitment	and	
goal	setting	in	bringing	about	changes	in	energy	use	is	expected	to	increase	once	used	in	combination	with	
other	type	of	interventions,	(Abrahamse	et	al.,	2005).	For	instance,	commitment	strategies	that	have	been	
combining	goal	setting	with	feedback	appear	to	be	more	effective	than	using	goal	setting	alone,	(McCalley	
&	Midden,	2002).	Commitment	strategies	have	been,	for	example,	successfully	applied	to	reduce	household	
energy	 use,	 especially	 in	 the	 long-term,	 as	 found	 in	 several	 studies,	 (Abrahamse	 et	 al.,	 2005).	 Similarly	
McCalley	and	Midden	(2002),	found	that	participants	who	had	been	given	a	goal	as	well	as	feedback,	saved	
more	 energy	 per	 washing	 trial,	 than	 participants	 who	 had	 only	 received	 feedback	 (without	 a	 goal).	 In
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addition	to	this,	Becker	(1978),	highlighted	the	care	one	should	have	in	defining	goals.	During	this	study,	
households	were	either	given	a	relatively	difficult	goal	(20	percent),	or	a	relatively	easy	goal	(2	percent),	to	
reduce	electricity	use.	The	results	suggest	that	an	easier	goal	appears	not	to	be	effective,	as	a	2	percent	
reduction	 may	 be	 perceived	 as	 not	 being	 worth	 the	 effort.	 Finally,	 previous	 research	 found	 that	 there	
appeared	to	be	no	significantly	different	behaviour	between	participants	who	had	been	able	to	set	a	goal	
and	those	with	an	assigned	goal,	(Abrahamse	et	al.,	2005;	Becker,	1978;	Bittle	et	al.,	1979;	Brandon	&	Lewis,	
1999;	Gerdes,	2009).	
In	 summary,	 commitment,	 goal	 setting	 and	 feedback	 appear	 to	 be	 viable	 mechanisms	 for	 reducing	
household	energy	use	and,	especially,	in	view	of	realising	long-term	behavioural	changes,	(Abrahamse	et	al.,	
2005);	and	particularly	when	used	in	combination,	(McCalley	&	Midden,	2002).	
4.4.3 	Behavioural	intervention	through	design	
As	has	been	explored	and	demonstrated	in	previous	sections,	infrastructures	and	technologies	are	at	the	
core	of	energy	consumption,	whether	that	is	cooking,	bathing	or	surfing	the	internet,	but	these	also	lock	
people	into	behaviours	that	can	be	very	difficult	to	change,	(Maréchal,	2010;	Southerton	et	al.,	2011),	as	
has	been	shown	in	Chapter	Two.	Thus,	behavioural	interventions	might	make	use	of	environmental	design,	
or	 material	 context	 adjustments	 that	 focus	 on	 the	 introduction	 of	 devices,	 or	 objects,	 that	 create	
opportunities	for	a	desired	behaviour	modification,	such	as	pro-environmental	behaviour,	more	salient,	or	
convenient.	This	is	also	known	as	choice	architecture	and	the	concept	of	nudge,	where	the	default	options	
are	set	in	order	to	facilitate	the	selection	of	the	individual’s	best	choice,	(Thaler	&	Sunstein,	2008),	through	
changes	in	the	context	in	which	they	are	made.	According	to	Grist	(2010),	nudging	is	of	particular	use	to	
influence	habitual	behaviours.	To	facilitate	better	decision	making	in	individuals,	Nudge	approaches	can	use	
product	design	as	a	mechanism	to	nudge	behaviour	in	a	particular	direction	in	specific	contexts.	An	example	
of	nudging	can	be	seen	in	Portland,	USA,	where	the	timing	of	traffic	signals	were	changed	in	a	way	that	was	
supposed	to	allow	a	reduction	in	petrol	use	by	motorists,	(Southerton	et	al.,	2011).	The	Portland	case	thus	
illustrates	how	nudging	can	be	used	without	individuals	having	to	make	a	choice,	or	necessarily	aware	that	
they	 have	 been	 ‘nudged’.	 Another	 example	 of	 nudging	 is	 the	 default	 opt-in	 for	 discretionary	 charges	 to	
finance	carbon	offsetting	schemes,	(Southerton	et	al.,	2011),	or	the	default	of	a	TV,	or	power	box,	from
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stand-by	to	off.	In	this	way,	choice	architecture	can	contribute	to	framing	individual	options	by	making	it	
easier	 for	 people	 to	 adopt	 the	 desired	 rather	 than,	 the	 undesired	 behaviour,	 (Dobson,	 2011;	 Thaler	 &	
Sunstein,	2008).	Nevertheless,	there	are	some	critics	to	the	nudging	approach.	For	instance,	Dobson	(2011),	
argues	 that	 nudging	 fails	 to	 engage	 people	 at	 the	 level	 of	 principle	 and,	 could	 be	 considered	 as	 a	
paternalistic,	anti-democratic	approach	to	changing	behaviour	without	prior	knowledge.	This	will	be	further	
examined	in	Chapter	8	when	it	comes	to	perceived	requirements	(RQ3a)	and	individual	perceptions	on	the	
effectiveness	 of	 intervention	 strategies	 (RQ3b).	 Dobson	 (2011),	 further	 argues	 that	 though	 nudging	 is	
perceived	as	a	‘low-cost’	and	‘low	pain’	strategy,	this	actually	might	not	necessarily	be	the	case.	
Physical	infrastructures	are	also	an	important	design	element,	since	they	support	the	development	of	social	
context,	 of	 the	 norms	 of	 consumption	 and	 is	 prominent	 in	 energy,	 building,	 transport,	 water	 and	
waste/recycling	 sectors,	 (Southerton	 et	 al.,	 2011).	 Shove	 and	 Southerton	 (2000),	 provided	 one	 example	
with	the	introduction	of	the	freezer	within	households,	which	has	developed	alongside	an	entire	frozen-
food	 infrastructure.	 This	 has	 resulted	 in	 changes	 to	 the	 design	 and	 use	 of	 houses	 and	 kitchens,	 the	
development	of	the	out-of-town	supermarkets	and	a	subsequent	decline	of	local	food	stores,	which	in	turn	
render	 household	 food	 provisioning,	 without	 a	 freezer,	 increasingly	 difficult.	 Shifting	 infrastructure	 thus	
holds	a	significant	potential	to	facilitate	individual	decision-making	and	to	shift	social	norms	toward	more	
sustainable	behaviours.	As	such,	interventions	in	material	infrastructures	not	only	create	the	conditions	for	
new	 habits	 to	 emerge,	 but	 they	 also	 hold	 the	 potential	 to	 lock	 people	 into	 sustained	 environmentally	
friendly	 behaviour.	 The	 main	 constraint	 with	 regards	 to	 intervention	 relates,	 consequently,	 to	 the	
infrastructure	and	cost	involved	in	establishing	those,	as	has	been	discussed	in	section	4.3.2.	
4.4.4 	Rewards	and	punishments	
Reward	and	punishment	approaches	appeal	to	people’s	self-interest	and	can	be	effective	in	the	short	term.	
Individuals	 have	 an	 apparent	 natural	 tendency	 to	 avoid	 losses,	 rather	 than	 to	 seek	 gains,	 (Kahneman	 &	
Tversky,	1979).	They	discount	future	gains	more	than	future	losses,	(Thaler,	1981),	prefering	to	have	short	
term	gains	rather	than	long	term	ones,	(Nordlund	&	Garvill,	2002,	2003;	Stern,	2000;	Thøgersen	&	Ølander,	
2002)	and	they	tend	to	give	preference	to	taking	action	where	these	create	potential	gains,	rather	than	
taking	action	to	avoid	potential	losses,	(Tversky	&	Kahneman,	1991).	With	this,	the	logic	behind	the	reward
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and	punishment	approach	is	simply	to	avoid	pain	(punishments)	and	embrace	pleasure	(rewards).	As	long	
as	 the	 incentives	 and	 disincentives	 are	 aligned	 with	 the	 goal,	 the	 adoption	 of	 different	 behaviours	 is	
evaluated	as	possible.	Dobson	(2011)	highlighted	two	main	benefit	of	this	approach:	it	can	work	very	fast,	
often	resulting	in	observable	positive	outcomes	as	soon	as	a	charge	and	incentive	measure	is	put	in	place	
and,	people	do	not	need	to	agree	with	the	environment	agenda	for	it	to	work.	Acceptance	might	be	an	
issue	in	particular	in	the	case	of	taxes,	charges,	or	fees.	As	an	example,	a	BBC	World	Service	Poll	(2007),	
survey	 showed	 that	 50	 percent	 of	 responders’	 were	 in	 favour	 of	 raising	 taxes	 on	 energy	 sources	 that	
contribute	 to	 climate	 change,	 whilst	 44	 percent	 opposed	 this.	 Acceptance	 levels	 did,	 however,	 increase	
once	it	was	noted	that	the	revenues	of	those	taxes	would	be	devoted	to	improving	efficiency	and	seeking	
out	sources	of	energy	that	do	not	produce	climate	change,	or	if	other	taxes	were	reduced	in	line,	so	that	the	
total	 tax	 bill	 remain	 the	 same.	 Less	 agreement	 seems	 to	 exist	 regarding	 the	 effectiveness	 of	 financial	
incentives.	 Southerton	 et	 al.	 (2011),	 highlighted	 that	 financial	 incentives	 often	 interfere	 with	 market	
mechanisms,	 supporting	 earlier	 findings	 from	 Thøgersen	 and	 Møller	 (2008)	 that	 illustrate	 that	 financial	
incentives	do	not	necessarily	foster	long	term	changes	in	behaviour,	once	the	incentive	is	removed.	Even	
though	there	is	evidence	that	rewards	seem	to	have	a	positive	effect	on	energy	saving	and	have	effectively	
encouraged	energy	conservation,	there	is	less	evidence	that	this	is	not	a	short-term	effect	and	that	desired	
behaviours	are	not	dropped	to	baseline	levels	once	the	reward	contingency	is	discontinued,	(Abrahamse	et	
al.,	2005;	Dwyer	et	al.,	1993;	Geller,	2002;	Geller	et	al.,	1982).	Dobson	(2011)	suggested	that	a	reason	for	
such	a	reversal	might	be	the	fact	that	the	strategy	seems	to	fail	to	engage	people	at	the	level	of	principle,	
since	 with	 punishments	 and	 rewards,	 people	 do	 not	 need	 to	 have	 any	 environmental	 commitment	
whatsoever	for	it	to	work.	This	is	to	say	that	what	initially	could	be	perceived	as	a	short-term	advantage	
with	immediate	impact,	can	actually	become	a	disadvantage	in	the	long-run,	due	to	the	fact	that	people	
respond	to	the	prompt	and	not	the	principles	underlying	it	(Dobson,	2011).	Nevertheless,	Geller	(2002),	
added	to	this	discussion	by	suggesting	that	relapses	can	also	result	from	interventions	that	were,	relatively,	
short	 in	 duration	 and	 not	 in	 place	 long	 enough	 to	 lead	 to	 long-term	 behaviour	 change.	 In	 contrast,	
strategies	geared	towards	punishment	seem	to	have	been	more	successful	in	enforcing	change,	such	as	
monetary	penalties	discouraging	unwanted	behaviours,	i.e.	the	London	congestion	charge.	Nevertheless,	
this	might	be,	again,	of	short-term	impact,	as	(Dobson,	2011),	studies	of	the	London	congestion	charge	have	
shown	that	after	an	initial	period	of	traffic	reduction,	levels	increased	again.	This	relapse	potential	perhaps
4.	Energy	use	and	intervention	strategies	
	
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also	 explains	 why,	 in	 recent	 years,	 less	 focus	 has	 been	 placed	 on	 environmental	 interventions	 that	 use	
reward	 schemes	 to	 incentivise	 change.	 During	 the	 1970’s,	 reward	 over	 punishment	 strategies	 were	 a	
popular	 component	 of	 environmental	 interventions	 due	 to	 the	 negative	 attitudes	 and	 counter-control	
measures	 that	 can	 result	 from	 perceived	 punishment,	 (Brehm,	 1972;	 Skinner,	 1971).	 55	 percent	 of	 the	
interventions	reviewed	by	Geller	et	al.	(1982)	involved	the	use	of	tangible	rewards.	In	contrast,	only	27	
percent	of	the	studies	(15	of	54),	from	the	1980’s	reviewed	by	Dwyer	et	al.	(1993)	used	rewards,	compared	
to	13	percent	(4	of	32),	of	environmental	related	studies	published	since	1990.	
In	summary,	reward	and	punishment	systems	have	an,	apparent,	positive	and	viable	short-term	impact	but	
are	 less	 promising	 in	 the	 long-term,	 (Abrahamse	 et	 al.,	 2005;	 Dobson,	 2011;	 Dwyer	 et	 al.,	 1993;	 Geller,	
2002;	Geller	et	al.,	1982;	Nordlund	&	Garvill,	2002,	2003;	Southerton	et	al.,	2011;	Stern,	2000;	Thøgersen	&	
Møller,	 2008;	 Thøgersen	 &	 Ølander,	 2002).	 But,	 they	 might	 equally	 contribute	 to	 the	 disconnection	 of	
people	thinking	about	the	moral	and	ethical	dimension	of	sustainability	and	thus	reduce	the	potential	for	
social	 learning	 within	 the	 process	 (Dobson,	 2011).	 Rewards	 and	 punishments	 systems	 thus	 hold	 the	
potential	 to	 reduce	 the	 likelihood	 of	 sustainability	 being	 thought	 of	 in	 normative	 terms.	 Sustainability	
becomes	 a	 non-normative	 policy	 objective	 achieved	 by	 the	 mobilisation	 of	 a	 reductive	 view	 of	 human	
motivation	 (self-interested	 utility	 maximisation),	 without	 making	 reference	 to	 sustainability	 at	 all;	 so	
missing	 the	 principle	 and	 opportunities	 for	 long-term	 social	 learning.	 In	 addition	 to	 this,	 rewards	 and	
incentives	 might	 have	 a	 different	 impact	 depending	 on	 the	 household	 income.	 Household	 energy	 use	 is	
related	to	people’s	income,	with	wealthier	families	spending	more	on	energy	than	poorer	ones	(section	
2.2.5.).	 This	 punishment	 and	 reward	 system	 might	 have	 differing	 impacts	 dependant	 on	 the	 different	
income	groups	and	on	how	much	is	spent,	as	a	fraction	of	income	and/or	expenditure	and	is	likely	to	effects	
their	reaction	to	such	types	of	interventions.	Finally,	rewards	and	punishments	systems	do	not,	apparently,	
address	the	performance	context	of	habits,	(Maréchal,	2010),	thus	they	do	not	seem	to	take	into	account	
one	of	the	identified	barriers	to	energy	savings,	as	has	been	discussed	in	Chapter	three.	
4.4.5 	Learning	theories	and	modelling	
Modelling	is	a	way	to	provide	examples	of	desired	behaviour	to	encourage	learning	by,	trial	and	error	and	
by	observing	how	others	behave,	(Bandura,	1977b).	Modelling	thus	assumes	that	examples	will	be	followed
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once	they	are	understandable,	relevant,	meaningful	and	rewarding,	in	terms	of	positive	results	to	people.	
Evidence	regarding	the	use	of	modelling	in	energy	conservation	areas	seems	to	be	scarce.	In	studies	from	
the	 80s,	 Winett	 and	 Kagel	 (1984)	 and	 Winett,	 Leckliter,	 Chinn,	 Stahl,	 and	 Love	 (1985),	 demonstrated	 its	
utility	in	increasing	energy	saving	and	conservation	at	home,	at	least	in	the	short	term,	with	participants	
who	 viewed	 a	 20-minute	 video	 presentation	 of	 conservation	 behaviours	 significantly	 decreasing	 their	
residential	energy	use	by	10	percent	over	a	nine-week	period	 when	compared	to	controls.	Additionally,	
before	and	after	testing	revealed	a	significant	increase	in	knowledge	for	the	experimental	group,	but	not	for	
the	 control	 group.	 A	 follow-up	 study,	 one	 year	 later,	 showed,	 however,	 that	 the	 savings	 were	 not	
maintained,	thus	modelling	intervention	did	not	lead	to	a	long-term	behavioural	change.	More	recently,	
McMakin,	 Malone,	 and	 Lundgren	 (2002),	 used	 videotaped	 modelling,	 as	 part	 of	 a	 multi-component	
campaign,	to	reduce	home	energy	use	of	residents	at	military	bases;	this	proved	to	be	moderately	effective	
in	promoting	behavioural	change.		
4.4.6 	Social	learning	community	based	approaches	
Community-based	initiatives	appear	to	be	well	in	line	with	social	practice	theory,	(Giddens,	1984)	and	often	
seek	to	change	consumer	behaviour	by	influencing	social	norms,	by	focusing	in	on	the	importance	of	social	
networks	 for	 circulating	 information	 and	 expectations	 regarding	 appropriate	 behaviours.	 They	 seek	 to	
support	individual	efforts	in	order	to	live	more	sustainably	by	framing	what	it	is	that,	‘we’,	like	to	consume,	
as	well	as	what,	‘we’,	understand	to	be	appropriate,	or	inappropriate,	conduct,	(Southerton	et	al.,	2011).	
Within	 this	 structure,	 community	 based	 initiatives	 target	 behaviour,	 followed	 by	 careful	 analysis	 of	 the	
barriers	that	prevent	the	desired	behaviour,	leading	to	the	piloting	of	a	community-wide	intervention	plan,	
within	 a	 small	 segment	 of	 the	 community	 and	 finally,	 to	 the	 implementation	 and	 evaluation	 of	 a	
community-wide	 application,	 (McKenzie-Mohr,	 2000).	 Thus,	 the	 objective	 is	 to	 help	 reduce	 the	 gap	
between	current	intervention	strategies	and	to	optimize	the	conditions	to	enable	individuals	to	carry	out	
energy	 efficiency	 behaviour.	 Namely	 (1),	 people	 value	 energy	 efficiency	 measures	 more	 if	 the	 benefits	
remain	 directed	 to	 themselves;	 (2),	 energy	 use	 and	 savings	 must	 be	 visible;	 (3),	 goals	 and	 motives	 for	
energy	 efficiency	 measures	 must	 be	 provided;	 and	 finally	 (4),	 information	 must	 be	 personalized	 and	
presented	 in	 a	 clear	 way,	 (McMakin	 et	 al.,	 2002).	 One	 example	 of	 Community-based	 initiatives	 is	 the
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EcoTeams	 Program	 (ETP)	 that	 consists	 of	 small	 groups,	 e.g.	 neighbours,	 friends	 and	 families,	 who	 come	
together	once	every	month	to	exchange	information	about	energy-saving	options,	(Abrahamse	et	al.,	2005)	
and	to	receive	feedback	about	own	and	other	EcoTeams	energy	saving	practices.	Staats,	Harland,	and	Wilke	
(2004),	 suggest	 ETP	 could	 be	 a	 promising	 type	 of	 intervention,	 since	 it	 has	 been	 successful	 in	 reducing	
energy	 use	 in	 several	 domains,	 both	 shortly	 after	 the	 program	 and	 during	 a	 follow-up	 two	 years	 later.	
However	and	as	already	mentioned,	due	to	the	combined	set	of	interventions	that	is	often	used	within	ETP,	
it	is	difficult	to	attribute	success	to	a	single	intervention	domain,	(Abrahamse	et	al.,	2005).	Furthermore,	
ETP	 participants	 presumably	 were	 highly	 motivated,	 making	 it	 difficult	 to	 generalize	 results	 to	 wider	
populations	which	might	be	holding	different	levels	of	motivations	regarding	energy	use	and	energy	saving	
behaviour,	(Abrahamse	et	al.,	2005).	
4.5 	Combined	Structural/Psychological	interventions		
Some	 interventions	 identified	 within	 the	 literature,	 which	 appear	 to	 be	 a	 rather	 combined	 approach	 of	
structural	and	psychological	interventions,	follow	on	below.	
4.5.1 	Prompting	strategies	
Prompting	 strategies	 are	 verbal	 or	 written	 messages	 that	 designate	 desirable	 target	 behaviours	 and	
prompting	messages	are	considered	to	be	a	way	to	provide	information,	(Staats	et	al.,	2000).	Prompting	
strategies	 might	 be	 an	 attractive	 intervention,	 since	 they	 can	 be	 of	 relatively	 low	 cost	 and	 can	 have	
considerable	 impact	 if	 used	 properly.	 In	 accordance	 to	 Geller,	 Winett,	 and	 Everett	 (1982),	 prompting	
strategies	should	meet	a	number	of	conditions	so	as	to	maximize	their	effectiveness,	namely	that	the	target	
behaviour	should	be	easy	to	perform,	clearly	defined	and	that	the	message	is	displayed,	in	close	proximity,	
to	where	the	target	behaviour	can	be	performed.	In	addition	to	this,	messages	should	be	stated	politely	to	
avoid	eliciting	negative	reactions,	(Brehm,	1972;	Skinner,	1971)	and	labelled	in	such	a	way	as	to	provide	
information	 designed	 to	 help	 consumers	 make	 informed	 choices,	 (Shove,	 2004).	 To	 further	 increase	
effectiveness,	products	would	need	to	be	fully	and	consistently	labelled	so	as	to	provide	consistent	and	
comparative	 levels	 of	 information	 for	 consumers,	 (DGGE/IP-3E,	 2004).	 The	 general	 challenge	 for	 carbon
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labelling	 is	 to	 ensure	 that	 the	 information	 provided	 within	 the	 label	 is	 meaningful,	 easy	 to	 understand,	
standardised,	and	that	motivates	consumers	into	wanting	to	take	action,	(Southerton	et	al.,	2011).	
4.5.2 	Feedback	provision	
Feedback	involves	providing	information	to	participants	about	their	environment-relevant	behaviours	and	is	
thus	 similar	 to	 information	 provision.	 A	 distinctive	 difference	 to	 information	 provision	 is	 that	 feedback	
strategies	tend	to	be	more	tailored	so	to	make	the	consequences	of	behaviour	more	salient.	Feedback	in	
the	 energy	 use	 area	 could	 be,	 for	 example,	 to	 provide	 households	 with	 information	 about	 their	 energy	
consumption,	 or	 achieved	 energy	 savings,	 with	 the	 expectation	 that	 households	 can	 associate	 certain	
outcomes,	e.g.	energy	saving,	with	their	behaviour,	(Abrahamse	et	al.,	2005).	In	most	homes,	attempts	to	
understand	energy	use	have	been,	aptly,	compared	to	shopping	at	a	grocery	store	without	any	prices	on	
display	and	receiving	a	bill	at	the	end	of	a	month’s	worth	of	purchases,	(Kempton	and	Montgomery,	1982,	
Janda,	2011).		
Feedback	might	vary	in	frequency,	purpose	and	type,	(Darby,	2006;	Fischer,	2008).	First	of	all,	the	frequency	
of	feedback	is	associated	with	the	way	feedback	is	provided,	e.g.	monitoring	devices	can	provide	continuous	
feedback,	 compared	 to	 energy	 bills,	 which	 provide	 feedback,	 perhaps,	 on	 a	 monthly	 base.	 Secondly,	
feedback	can	also	be	provided	for	specific	households	or,	as	a	comparison	to	other,	similar	households,	
neighbours,	or	communities.	Feedback	about	individual	performance	relative	to	others	may	be	helpful	in	
reducing	household	energy	use	by	the	mediation	of	social	norms,	by	comparison	of	their	energy	use	to	that	
of	friends,	or	neighbours,	(Cialdini	et	al.,	1991;	Cialdini	et	al.,	1990;	Triandis,	1977).	Comparative	feedback	
could	thus	influence	the	perception	of	what	constitutes	‘normal’	energy	use	and	also	produce	a	feeling	of	
competition,	social	comparison,	or	social	pressure,	which	may	be	especially	effective	once	important,	or	
other	relevant	factors	are	used	as	a	reference	group,	(Steg,	Dreijerink,	&	Abrahamse,	2006).	Yet,	evidence	
appears	scarce	that	using	comparative	feedback	could	indeed	be	more	effective	than	individual	feedback,	
(Brandon	 and	 Lewis,	 1999).	 This	 impact	 might	 also	 be	 influenced	 by	 the	 way	 comparative	 feedback	 is	
provided.	This	is	to	say	that	when	people	become	aware	of	a	social	descriptive	norm	(what	is	done),	their	
behaviour	 tends	 to	 change	 to	 become	 closer	 to	 the	 norm,	 which	 could	 then	 negatively	 impacting	 those	
users	 that	 use	 less	 energy,	 as	 they	 might	 feel	 tempted	 to	 increase	 their	 energy	 use,	 (Brandon	 &	 Lewis,
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1999).	The	power	of	these	messages	can	nevertheless	be	harnessed	by	using	injunctive	norms	instead,	with	
messages	conveying	approval	of	particular	actions	considered	to	contribute	to	decrease	the	effect,	(Schultz,	
Nola,	Cialdini,	Goldstein,	&	Griskevicius,	2007).	Thirdly,	it	is	not	clear	whether	it	makes	any	difference	to	
give	 feedback	 in	 terms	 of	 monetary	 rather	 than	 environmental	 costs,	 since	 studies	 investigating	 this	
difference	did	not	find	any	evidence	for	this,	or	determination	as	to	which	could	be	more	meaningful	to	
recipients,	(Brandon	&	Lewis,	1999).	
4.5.3 	Monitoring	systems	and	metering	
The	‘invisibility’	of	energy	might	contribute	to	individual	unawareness	of	consumption	levels	and	fostering	
support	 towards	 measures,	 such	 as	 feedback	 on	 energy	 consumption	 and	 personal	 contribution,	 could	
provide	 an	 access	 to	 the	 problem	 of	 providing	 information,	 (Darby,	 2006;	 Roberts	 &	 Baker,	 2003).	
Monitoring	systems,	such	as	energy	meters,	could	be	seen	as	a	way	to,	‘commoditize,’	behaviour	into	a	
good	proxy,	in	order	to	make	consumption	visible,	(WWF,	2008).	Today's	monitoring	systems	offer	new	
opportunities	to	observe	and	give	feedback	to	people	and	to	engage	with	them,	in	real	time,	about	the	
complex	ways	in	which	they	consume	energy.	They	are	however	not	entirely	new	and	smart	metering,	for	
example,	was	initially	proposed	in	the	1970s,	though	only	recently	has	come	into	full	view,	(Darby,	2010).	
Recent	research	on	smart	metering	and	householder	engagement	agrees	that	feedback	alone	is	not	enough	
to	 interest	 occupants,	 (Darby,	 2010),	 but	 nevertheless,	 feedback	 strategies	 have	 shown	 modest,	 but	
consistent,	energy	savings,	although	some	exceptions	do	exist,	(Abrahamse	et	al.,	2005;	Dwyer	et	al.,	1993;	
Geller	et	al.,	1982).	Research	shows	that	in-home	displays	give	interested	users	feedback	information	to	
help	them	understand	and	manage	their	electricity	more	efficiently,	achieving	savings	in	the	range	of	5–15	
percent,	(EEA,	2013).	There	is	also	evidence	that	displays	have	an	enduring	impact,	even	if	only	used	for	
short	periods,	through	changed	habits	and	investment	in	efficiency	measures,	(Darby,	2006;	Rossini,	2009).	
Monitoring	systems	have	been	shown	that	feedback	efficacy	is	expected	to	be	influenced	by	the	time	that	
the	feedback	is	provided;	and	favouring	feedback	provision	immediately	after	the	behaviour	occurs,	(Geller,	
2002).	The	more	frequent	that	feedback	is	given,	the	more	effective	it	is	with	the	most	positive	effects	
being	observed	with	continuous	feedback,	(Abrahamse,	2003;	Abrahamse	et	al.,	2005).	However,	the	use	of	
energy	meters	has	been	under	discussion	since	their	acceptance	and	impact	levels,	apparently,	do	vary.	On
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one	 side,	 appreciation	 could	 be	 observed,	 but	 equally	 there	 had	 been	 annoyance,	 (Hargreaves,	 Nye,	 &	
Burgess,	2010;	IPPR,	2009).	In	addition	to	this,	the	impact	of	energy	meters,	in	terms	of	energy	saving,	is	
considered	 to	 decrease	 with	 time	 (EEA,	 2013)	 which	 is	 in-line	 with	 findings	 from	 Darby	 (2006),	 that	
feedback	on	consumption	could	have	an	impact,	but	might	not	be	sufficient	for	people	to	understand	and	
thus	change	their	behaviour	regarding	energy	saving.	Yet,	the	joint	use	of	feedback	and	commitment	could	
be	a	viable	way	to	achieve	impact,	(Maréchal,	2010;	Stern,	2000).	
4.5.4 	Social	marketing		
Social	 marketing	 can	 be	 defined	 as	 the	 application	 of	 marketing	 principles	 and	 tools	 to	 achieve	 socially	
desirable	goals,	(Andreasen,	1995;	Kotler	&	Zaltman,	1971).	Social	marketers	understand	that	behaviour	
change	 is	 the	 main	 goal	 and	 that	 to	 change	 behaviour	 it	 is	 not	 necessarily	 required	 to	 change	 people’s	
fundamental	attitudes	and	beliefs,	but	rather	to	work	within	their	current	attitudes	and	beliefs.	As	such	
social	marketing	opens	the	opportunity	to	promote	behavioural	change	based	on	existing	values	that	are	
not	necessarily	pro-environmental,	but	still	could	foster	more	sustainable	behaviours,	(Southerton	et	al.,	
2011).	Social	marketing	has	been	used	in	a	variety	of	areas	to	promote	individual	behavioural	change	and,	
in	particular,	to	provide	solutions	in	public	health	areas,	(Grier	&	Bryant,	2005;	Helmig	&	Thaler,	2010).	
Social	marketing	generally	promotes	voluntary	behavioural	change	based	on	building	beneficial	exchange	
relationships	with	a	target	audience	for	the	benefit	of	society,	(Schwartz,	B.	in	Hastings,	2008).	This	draws	
from	the	exchange	theory,	(Hastings	&	Haywood,	1991),	which	states	that	people	change	their	behaviour	
because	they	are	offered	something	in	exchange	that,	they	perceive,	provides	greater	benefits	and	fewer	
barriers	than	the	alternative.	As	a	result	individuals	will	take	action	to	adapt	as	it	is	in	their	interest	and	
ability	to	do	so.	That	is,	they	will	take	measures	where	the	benefits	outweigh	the	costs	to	them.	As	such,	
promoting	individual	change	requires	an	understanding	of	some	of	the	relevant	principles	which	are	the	
core	 of	 social	 marketing:	 the	 target	 population,	 segmentation	 of	 the	 population	 and	 aligning	 change	
interventions	to	specific	segments.	With	this,	the	principle	of	change	is	clearly	distinct	from	the	regulatory,	
or	 the	 education	 principle,	 (Andreasen,	 1995),	 as	 the	 regulatory	 principle	 focuses	 on	 rewards	 and	
punishments,	 while	 the	 education	 principle	 assumes	 that	 people	 modify	 behaviour	 as	 they	 acquire	
information	or	skills	that	they	did	not	previously	have.	Voluntary	behavioural	change	also	means	that	there
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is	no	coercion	and	as	such,	it	does	not	exclude	the	Nudge	approach,	since	changing	the	conditions	in	which	
behaviour	 occurs	 is	 not	 viewed	 as	 coercion	 as	 individuals	 are	 allowed	 to	 choose.	 Contrarily,	 choice	
architecture	should	rather	be	seen	as	a	tool	for	making	the	‘right’	individual	decision	as	easy	as	possible	for	
people	to	do.	
The	history	of	commercial	marketing	shows	that	knowing	and	segmenting	one’s	audiences	is	a	precondition	
for	 success.	 Behavioural	 change	 interventions	 that	 are	 drawing	 on	 social	 marketing	 thus	 need	 to	 be	
targeted	at	specific	segments	of	the	population.	For	example,	in	the	case	of	adopting	more	energy	efficient	
behaviour	one	would	have	to	take	into	consideration	the	existing	needs,	barriers	and	motivations	to	save	
energy,	 actions	 already	 undertaken	 and	 those	 that	 individuals	 intend	 to	 take	 and	 accurately	 targeting	
segments,	 using	 messages,	 messengers,	 communications	 channels	 and	 policies	 that	 are	 appropriate	 to	
them,	 (Leiserowitz	 et	 al.,	 2009;	 Southerton	 et	 al.,	 2011).	 Whilst	 similar	 to	 commercial	 marketing,	 social	
marketing	 works	 on	 the	 principle	 of	 population	 segmentation	 using	 the	 4Ps	 (product,	 price,	 place	 and	
promotion).	 These	 are	 the	 basic	 structural	 elements	 that	 social	 marketing	 addresses	 to	 produce	 a	
competitive	benefit	for	a	particular	segment	of	the	audience,	once	orientated	through	the	market	exchange	
filter,	 (Grier	 &	 Bryant,	 2005;	 Weinreich,	 1999),	 aimed	 at	 changing	 individual	 behaviour	 and	 attitudes,	
(Andreasen,	1995;	G.	Hastings	&	Saren,	2003;	Helmig	&	Thaler,	2010;	Kotler	et	al.,	1989).	The	basic	idea	is	to	
rebalance	the	4Ps	mix	compensating	for	missing	or	weak	Ps.	The	difference	between	commercial	and	social	
marketing	is	in	what	the	4Ps	stand	for.	For	social	marketing	the	4Ps	have	the	following	objectives:	
• ‘Product’	means	the	social	proposition,	the	desired	behaviour	one	is	asking	the	audience	to	adopt,	
the	associated	benefits	of	adopting	the	desired	behaviour	and	any	tangible	objects,	or	services,	
which	support,	or	facilitate,	the	desired	behaviour.	
• ‘Price’	means	the	cost	of	involvement	and	also	the	barriers	that	the	target	audience	needs	to	face	
once	changing	towards	the	desired	behaviour.	Non-monetary	costs	such,	as	time,	should	also	be	
considered.	 Here	 is	 where	 the	 exchange	 principle	 is	 important,	 since	 the	 benefits	 of	 changing	
behaviour	should	be	greater	than	the	costs.
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• ‘Place’	 stands	 for	 accessibility,	 either	 the	 location	 where	 the	 target	 audience	 will	 perform	 the	
desired	behaviour,	or	where	the	product,	or	service,	is	made	available	to	the	target	audience.	
• ´Promotion’	 covers	 communication,	 how	 the	 product,	 or	 service,	 is	 made	 known	 to	 the	 target	
segment.	For	the	energy	area,	the	product	is	rather	the	adoption	of	new	behaviour	regarding	the	
usage	 of	 energy	 consuming	 appliances	 and	 actions	 and	 not	 just	 of	 purchasing	 new	 appliances,	
(Peattie	&	Peattie,	2003).	
The	academic	literature	on	social	marketing,	behaviour	change,	and	even	commercial	branding,	suggests	
that	 people	 are	 motivated	 to	 purchase	 products	 and/or	 change	 their	 behaviour	 based	 on	 three	 broad	
categories	of	benefits,	(Leiserowitz	et	al.,	2009).	These	are;	(1),	functional	benefits:	what	the	product,	or	
behaviour,	will	do;	(2),	self-expressive	benefits:	what	the	product,	or	behaviour,	says	about	one;	and	(3),	
self-evaluative	benefits:	how	the	product,	or	behaviour,	makes	one	feel	about	themselves.	Leiserowitz	et	al.	
(2009),	further	proposed	that	functional	benefits	are	ones	that	are	relatively	simple	to	promote	and	that	
promotional	 communication	 campaigns	 need	 only	 to	 invoke	 the	 functional	 benefits	 of	 the	 product,	 or	
behaviour	that	members	of	the	target	audience	find	most	persuasive.	On	the	other	side,	self-expressive	and	
self-evaluative	benefits,	though	being	more	challenging	to	promote,	are	often	more	powerful	and	of	longer	
duration.	Enhancing	the	functional	benefits	of	saving	energy	could	therefore	involve	messages	such	as,	‘It	
will	save	me	money’,	as	those	seem	to	be	at	the	centre	of	individual	motivation	to	save	energy.	Enhancing	
self-expressive	benefits,	on	the	other	hand,	might	involve	messages	such	as,	‘I’m	the	kind	of	person	who	
cares	about	helping	to	reduce	global	warming’,	while,	associated	self-evaluative	benefits	might	including,	‘I	
feel	good	about	myself	once	I	do	this	because	it’s	the	moral	thing	to	do’.	
Judging	from	the	literature,	there	appears	to	be,	however,	three	limitations	to	the	use	of	social	marketing	in	
the	 energy	 area.	 Firstly,	 a	 relation	 between	 the	 success	 and	 failure	 of	 behavioural	 change	 interventions	
could	be	influenced	by	the	ability	to	remove	barriers	that	currently	impede	target	audience	members	from	
performing	recommended	behaviours,	(Leiserowitz	et	al.,	2009).	As	such,	enhancing	individuals’	motivation	
to	change	is	necessary,	but	likely	won’t	be	sufficient	alone	and	in	order	for	the	recommended	behaviour	to	
be	widely	adopted,	there	will	also	be	a	need	to	remove	the	barriers	that	individuals	face.	In	Chapters	2	and	
3,	a	number	of	such	barriers	towards	more	pro-environmental	behaviour,	more	specifically	towards	less
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energy	intensive	ones,	have	been	discussed	and	removing	those	barriers	was	seen	to	require	addressing	
cultural,	normative	and	individual	psychological	variables	that	are	often	hard	to	change.	Secondly,	the	social	
marketing	approach	might	actually	serve	to	defer,	or	even	undermine,	the	prospects	for	more	far-reaching	
and	systemic	behavioural	changes	that	are	needed	in	the	area	of	energy	consumption.	According	to	the	
WWF	(2008),	this	is	to	say	that	social	marketing	might	lead	to	feelings	of	uncertainty,	despair	and	guilt,	
contributing	 to	 states	 of	 denial,	 paralysis	 and	 apathy	 resulting	 in	 people	 feeling	 helpless	 in	 regards	 to	
adopting	more	energy	efficient	behaviour,	as	discussed	within	section	3.4.3.	Thirdly,	in	the	case	of	energy,	
there	 might	 be	 no	 visible,	 direct	 benefit	 of	 saving	 energy.	 It	 is	 difficult	 for	 individuals	 to	 perceive	 the	
benefits	of	the	social	good	that	social	marketing	intervention	promotes.	As	such,	the	use	of	social	marketing	
within	the	energy	consumption	area	might	look	for	inspiration	in	other	related	areas,	such	as	reducing	the	
number	 of	 non-voters	 during	 elections,	 or	 donation	 campaigns.	 Kotler	 et	 al.	 (1989),	 recognized,	 for	
example,	 that	 social	 marketing	 campaigns	 could	 have	 limited	 success	 in	 promoting	 behavioural	 change,	
since	individuals,	even	if	aware	of	the	consequences	of	their	behaviour,	might	lack	motivation,	or	ability,	or	
simply	because	the	competitive	behaviour	is	more	attractive.			
4.6 	Concluding	remarks	
As	has	been	discussed	throughout	this	chapter,	achieving	lasting	behavioural	change	might	be	a	difficult	
undertaking,	 in	 particular	 since	 environmental	 values,	 beliefs	 and	 attitudes	 apparently	 do	 not	 have	 any	
significant	influence	on	energy	consumption.	It	can	also	be	seen	that	there	are	a	number	of	frameworks	
that	attempt	to	support	intervention	strategies,	by	trying	to	find	the	right	interplay	between	the	various	
strategies	each	showing	a	slight	variation	in	terms	of	existing	factors	and	approach.	This	includes	the	right	
interplay	 between	 contextual	 factors	 and	 micro-level	 factors,	 plus	 a	 diversity	 of	 other	 determinants,	
motivations	and	barriers	that	may	need	to	be	taken	into	account	for	any	successful	intervention	attempt.	It	
has	 been	 discussed	 that	 there	 are	 a	 number	 of	 potential	 intervention	 layers	 and	 that	 any	 type	 of	
intervention	might	also	have	to	take	into	account	the	role	of	communication	and	persuasion,	so	that	the	
credibility	 of	 the	 sender,	 the	 persuasiveness	 of	 the	 argument/message,	 or	 the	 responsiveness	 of	 the	
audience	can	be	assured.	The	literature	shows	a	diversity	of	existing	intervention	strategies	and	types	that	
could	 be	 broadly	 grouped	 into	 either,	 structural	 or,	 psychological	 interventions.	 While	 structural
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interventions	aim	to	change	the	(social),	context	in	which	behavioural	decisions	take	place,	psychological	
intervention	aims	at	changing	existing	perceptions,	knowledge,	attitudes,	norms	and	values	(i.e.	individual,	
micro-level	 variables).	 To	 date	 however,	 most	 intervention	 strategies	 have	 predominantly	 focused	 on	
voluntary	behavioural	change,	rather	than	on	changing	contextual	factors	aimed	at	determining	individual	
decisions.	 The	 difference	 here	 is,	 that	 contextual	 factors	 set	 the	 context	 where	 individual	 decisions	 are	
made	 and	 intervention	 strategies	 that	 include	 both,	 voluntary	 behaviour	 change	 and	 contextual	 factors,	
might,	therefore,	increase	the	level	of	success	in	promoting	lasting	behavioural	change.	Despite	a	growing	
body	 of	 research	 and	 evidence,	 there	 still	 appears	 to	 be	 no	 clear	 evidence	 for	 the	 potential	 long-term	
effectiveness	of	change	interventions	within	the	field	of	home	energy	use	which	this	research	attempts	to	
explore	 further	 in	 Chapter	 8.	 In	 regard	 to	 this,	 it	 can	 also	 be	 seen	 that	 there	 are	 numerous	 persuasion	
theories	 that	 might	 be	 applied	 to	 promote	 behavioural	 change,	 with	 each	 one	 providing	 a	 different	
approach	that	could	be	useful.	Chapter	8	will	thus	investigate	how	such	possible	approaches,	factors	and	
determinants	might	be	best	considered	within	interventions	(RQ3b)	and	what	these	requirements	might	be	
(RQ3a).
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5 	Research	methodology	and	design	
This	chapter	discusses	the	methodological	approaches	taken	in	the	research	study.		It	also	considers	other	
theoretical	applicable	methodologies	and	reasons	for	discounting	these	approaches.	The	chapter	provides	
an	 overview	 of	 the	 research	 design,	 the	 methods	 used	 to	 address	 research	 questions	 and	 details	 how	
research	 questions	 have	 been	 derived	 from	 previous	 literature	 review	 chapters.	 An	 overview	 of	 the	
research	design	is	shown	in	Figure	5-1	outlining	the	relation	between	the	different	phases	of	research.		
	
Figure	5-1:	Research	design	from	initial	framing	to	implementation.	
This	research	is	of	an	exploratory	nature	and	aims	to	explore	how	the	adoption	of	more	energy	efficient	
behaviours	at	home	could	be	encouraged.	With	this	the	research	has	the	objective	to	gain	an	understanding	
of	energy	use	at	home	and	how	the	adoption	of	more	energy	efficient	behaviours	could	be	promoted.	The	
methodological	approaches	chosen	for	this	study	thus	must	be	compatible	with	the	exploratory	nature	of	
the	research	and	to	support	answering	the	overall	research	questions:	
• RQ1:	What	explains	energy	use	at	home?	
• RQ2:	What	influences	energy	use	at	home?
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• RQ3:	How	to	promote	energy	efficient	behaviour?	
As	can	be	seen	from	the	questions,	this	research	does	not	attempt	to	test	existing	theories,	but	to	obtain	an	
insight	and	in-depth	knowledge,	of	the	topic	under	investigation	through	the	different	phases	of	research.	
The	 study	 targets	 both	 energy	 users	 and	 energy	 conservation	 intervention	 practitioners	 in	 the	 area	 of	
energy	 efficiency,	 so	 to	 provide	 a	 more	 comprehensive	 and	 complete	 overview	 of	 potential	 behavioural	
interventions	that	would	result	in	the	adoption	of	more	energy	efficient	behaviour.		
5.1 Literature	review	on	available	methods		
The	 methodological	 approaches	 chosen	 for	 this	 study	 have	 been	 selected	 based	 upon	 the	 exploratory	
nature	of	the	research	and	after	careful	evaluation	and	consideration	of	the	possible	theoretical	applicable	
methodologies	that	are	available.	
5.1.1 Inductive	or	deductive	
Through	 this	 research	 a	 preference	 has	 been	 given	 for	 inductive	 research,	 with	 the	 emphasis	 on	 an	
exploratory	approach	to	improve	the	understanding	of	energy	use	at	home	and	how	the	adoption	of	more	
energy	 efficient	 behaviour	 could	 be	 promoted.	 In	 an	 inductive	 approach	 theory	 is	 developed	 from	 the	
observation	 of	 empirical	 reality;	 which	 involves	 moving	 from	 individual	 observation	 to	 statements	 of	
general	patterns,	or	laws,	(Hussey	and	Hussey,	1997).	This	is	in	contrast	to	a	deductive	approach	where	a	
conceptual	and	theoretical	structure	is	developed	and	then	tested	by	empirical	observation,	so	to	move	
from	 the	 general	 to	 the	 particular,	 (Hussey	 and	 Hussey,	 1997).	 Empirical	 research	 requires	 choosing	
between	the	deductive	or	inductive	research	paradigms.	Figure	5-2	demonstrates	the	differences	between	
these	two	paradigms	and	research	approaches.	
	
Figure	5-2:	Inductive	vs.	deductive	research	approaches,	(Rudestam,	Newton,	2001,	p.5).
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As	this	research	has	been	placing	an	emphasis	on	an	exploratory	approach	an	inductive	approach	has	thus	
seen	to	be	more	appropriate	to	improve	the	understanding	of	energy	use	at	home	and	how	the	adoption	of	
more	energy	efficient	behaviours	could	be	promoted.	
5.1.2 Subjective	or	objective	
Another	decision	that	had	to	be	taken	relates	to	the	question	of	subjectivity	and	objectivity,	which	means	
the	extent	to	which	the	researcher	is	subjective	(involved	in	or	has	an	influence	on	the	research	outcome)	
or	objective	(distanced	from	or	independent)	in	the	execution	of	the	fieldwork	(empirical	work).	Easterby-
Smith	 et	 al.	 (2002)	 and	 Tashakkori	 &	 Teddlier	 (2003)	 both	 discussed	 the	 traditional	 assumption	 that	 in	
science	the	researcher	must	maintain	complete	independence	if	there	is	to	be	any	validity	in	the	results	
produced.	However,	within	this	research,	the	researcher	seeks	to	explore	and	understand	the	narratives	
built	 around	 energy	 use	 at	 home,	 uncovering	 the	 perceptions	 of	 reality,	 which	 is	 by	 its	 very	 nature,	
subjective.	It	is	accepted	that	such	a	subjective	approach,	as	used	in	the	research,	requires	the	recognition	
of	any	influence	or	limitation	such	subjectivity	may	have	on	the	conduct	or	findings	of	the	research.	It	is	
argued	that	the	selection	of	a	mixed	method	approach	with	the	inclusion	of	qualitative	methods	implies	the	
existence	of	a	subjective	approach	(Hussey	&	Hussey,	1997),	since	qualitative	data	is	subjective	by	nature	
since	different	people	can	perceive	the	truth	differently.	With	this,	the	researcher’s	experiences,	beliefs,	
and	 values	 are	 incorporated	 into	 the	 research	 design	 and	 analysis	 of	 data,	 with	 qualitative	 researchers	
studying	things	in	their	natural	settings,	attempting	to	make	sense	of,	or	interpret,	phenomena	in	terms	of	
the	meanings	people	bring	to	them.	
5.1.3 Positivism	or	constructivism	
Positivism	is	based	on	a	deductive,	scientific	process,	looking	for	a	cause	and	effect	relation,	drawn	from	an	
initial	hypotheses,	whereas	constructivism	is	by	nature	more	inductive,	based	on	the	interpretation	of	data	
to	generate	a	conclusion,	(Hussey	and	Hussey,	1997).	Within	the	inductive	approach	theory	is	developed	
from	the	observation	of	empirical	reality,	and	thus	it	is	constructed.	The	inductive	approach	is	thus	similar	
to	 constructivism	 in	 so	 far	 as	 constructivism	 uses	 inductive	 reasoning.	 From	 a	 constructivist	 perspective	
knowledge	is	developed	through	the	interaction	with	the	natural	world	(Glasersfeld,	1990;	Piaget,	1952;	
Piaget,	 1969).	 	 Knowledge	 is	 thus	 not	 passively	 received	 but	 it	 is	 actively	 constructed	 through	 social
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interaction	 and	 it	 has	 an	 important	 influence	 on	 the	 formation	 of	 language,	 thought,	 and	 finally	 of	
personality.	(Vygotsky	1978).	In	accordance	with	Piaget	(1952)	knowledge	is	not	a	representation	of	the	real	
world,	 but	 instead	 a	 collection	 of	 conceptual	 structures	 that	 results	 from	 the	 development	 of	 human	
intellect	and	proceeds	through	adaptation	and	organization.	The	existing	knowledge	of	an	individual	is	thus	
a	result	of	past	and	existing	experiences	(Glasersfeld,	1989).	
This	research	further	combines	positivist	and	constructivist	paradigms,	as	use	of	both	paradigms	was	seen	
to	be	an	appropriate	means	to	provide	the	researcher	with	the	ability	to	statistically	analyse	the	data,	whilst	
also	allowing	for	an	exploration	of	the	complex	set	of	variables	that	influence	human	behaviour.		
5.1.4 Qualitative	or	quantitative	
Empirical	research	requires	choosing	whether	to	adopt	a	quantitative	or	qualitative	approach,	or	some	mix	
of	the	two.	If	in	one	way,	quantitative	research	aims	at	generating	statistics	through	the	use	of	methods	
such	 as	 surveys	 or	 structure	 interviews,	 qualitative	 research	 aims	 at	 exploring	 attitudes,	 behaviour	 and	
experiences	 through	 such	 methods	 as	 interviews	 or	 focus	 groups	 (Dawson,	 2002).	 A	 quantitative	 study,	
consistent	with	the	quantitative	paradigm,	is	an	inquiry	into	a	social	or	human	problem,	based	on	testing	a	
theory	composed	of	variables,	measured	with	numbers,	and	analysed	with	statistical	procedures,	in	order	
to	determine	whether	the	predictive	generalizations	of	the	theory	hold	true.	In	contrast,	a	qualitative	study	
is	 an	 inquiry	 process	 of	 understanding	 social	 or	 human	 problem,	 based	 on	 building	 a	 complex,	 holistic	
picture,	 formed	 with	 words,	 reporting	 detailed	 views	 of	 informants,	 and	 conducted	 in	 a	 natural	 setting	
(Cresswell,	2009).	The	purpose	of	qualitative	research	is	to	examine	the	patterns	of	meaning	which	emerge	
from	the	data	and	these	are	often	presented	in	the	participants'	own	words.	The	task	of	the	qualitative	
researcher	is	to	find	patterns	within	those	words	(and	actions)	and	to	present	those	patterns	for	others	to	
inspect	while	at	the	same	time	staying	as	close	to	the	construction	of	the	world	as	the	participants	originally	
experienced	 it.	 Denzin	 and	 Lincoln	 (2002)	 point	 out	 that	 qualitative	 research	 is	 multi-method	 in	 focus,	
involving	an	interpretive,	naturalistic	approach	to	its	subject	matter.	This	means	that	qualitative	researchers	
study	things	in	their	natural	settings,	attempting	to	make	sense	of	or	interpret	phenomena	in	terms	of	the	
meanings	people	bring	to	them	by	the	use	of	a	variety	of	empirical	materials.	This	constructivist	notion	that	
reality	is	changing	whether	the	observer	wishes	it	or	not	is	an	indication	of	multiple	or	possibly	diverse
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constructions	of	reality.	Constructivism	values	multiple	realities	that	people	have	in	their	minds.	Therefore,	
to	acquire	valid	and	reliable	multiple	and	diverse	realities,	multiple	methods	of	searching	or	gathering	data	
are	 in	 order	 and	 the	 use	 of	 investigators,	 method	 and	 data	 triangulations	 to	 record	 the	 construction	 of	
reality	is	appropriate	(Creswell	&	Clark,	2007).		
In	 accordance	 to	 the	 literature,	 (Creswell	 and	 Clark,	 2007;	 Morse,	 2003),	 the	 use	 of	 quantitative	 and	
qualitative	 approaches	 in	 combination	 also	 provides	 a	 better	 understanding	 of	 research	 problems	 than	
either	 approach	 used	 alone.	 It	 can	 help	 answer	 questions	 that	 cannot	 be	 answered	 by	 quantitative	 or	
qualitative	 approaches	 alone,	 which	 was	 seen	 as	 relevant	 and	 to	 support	 the	 nature	 of	 this	 research.	
Quantitative	methods	appear	to	be	in	particular	suitable	to	address	a	large	population	and	thus	produce	
results	 that	 are	 easy	 to	 code	 and	 standardize,	 (D.	 Morgan,	 2007;	 Wilkinson	 &	 Birmingham,	 2003).	 Such	
quantitative	 approaches	 are	 however	 limited	 to	 provide	 in-depth	 and	 detailed	 information	 and	 thus	
qualitative	 methodologies	 were	 subsequently	 used	 to	 explore	 the	 topic	 in	 more	 detail	 and	 to	 allow	 the	
voice,	concerns	and	practices,	of	research	participants	to	be	heard,	(Cole,	2006;	Weaver	and	Olson,	2006).	
Using	narratives	and	qualitative	methods	appeared	to	be	however	more	adequate	to	better	understand	
everyday	energy	practices,	with	structured	questionnaires	to	gather	a	broader	spectrum	of	data.	As	this	
research	 seeks	 to	 understand	 people	 and	 the	 social	 and	 cultural	 contexts	 within	 which	 they	 live,	 the	
qualitative	 approach	 of	 data	 gathering	 had	 thus	 been	 dominant	 throughout	 this	 study.	 Quantitative	
research	in	this	study	is	therefore	aimed	to	gain	insight	and	identify	issues	for	the	subsequent	qualitative	
phases	 of	 the	 empirical	 work,	 while	 the	 qualitative	 research	 aims	 to	 explore	 attitudes,	 behaviour	 and	
experiences	through	such	methods	as	interviews	or	focus	groups.		
The	use	of	both,	qualitative	and	quantitative	methodologies	allowed	the	researcher	to	embrace	different	
aspects	of	energy	related	behaviours,	as	well	as	to	address	their	diversity	and	complexity	so	as	to	better	
understand	the	meaning	that	people	assign	to	energy	use,	exploring	the	full	complexity	of	determinants	
that	 influence	 energy	 use,	 and	 to	 increase	 general	 understanding	 on	 how	 the	 adoption	 of	 more	 energy	
efficient	behaviours	could	be	promoted.	The	use	of	both	groups	of	methods	also	supports	the	reliability,	
validity	and	quality	of	the	findings,	since	 both	qualitative	and	quantitative	researchers	need	to	test	and	
demonstrate	that	their	studies	are	credible	(Golafshani,	2003).	With	this	the	use	of	triangulation,	a	means	
of	combining	qualitative	and	quantitative	research	methods,	could	be	seen	as	a	viable	approach	to	allow	for
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the	“convergence	among	multiple	and	different	sources	of	information	to	form	themes	or	categories	in	a	
study”	(Creswell	&	Miller,	2000,	p.	126)	and	to	reflect	the	multiple	ways	of	establishing	truth	(Golafshani,	
2003;	Bergmann,	2011).	Triangulation	can	be	a	means	to	overcome	the	influence	the	researcher	has	on	the	
behaviour	of	participants,	or	in	terms	of	the	bias	the	researcher	brings	himself	or	herself	into	the	conduct	of	
the	research	(Easterby-Smith,	Thorpe,	&	Lowe,	2002;	Patton,	2002).	
Triangulation	 therefore	 allows	 for	 an	 increase	 in	 the	 reliability,	 quality	 and	 validity	 of	 the	 findings,	
(Bergman,	2011;	Easterby-Smith	et	al.,	2002;	Golafshani,	2003;	Patton,	2002).	Triangulation	in	this	context	
was	 thus	 also	 seen	 as	 a	 means	 to	 overcome	 the	 influence	 that	 the	 researcher	 has	 on	 the	 behaviour	 of	
participants,	or	in	terms	of	the	bias	that	the	researcher	brings	into	the	conduct	of	the	research.	As	Hussey	&	
Hussey	(1997)	argued,	the	selection	of	a	mixed	method	approach	with	the	inclusion	of	qualitative	methods	
implies	the	existence	of	a	subjective	approach,	since	qualitative	data	is	subjective	by	nature	as	different	
people	 can	 perceive	 the	 truth	 differently.	 Further	 to	 this	 the	 research	 used	 some	 of	 the	 triangulation	
categories	proposed	by	Stake	(1995),	namely	data	and	methodological	triangulation	and	multiple	methods	
like	surveys,	focus	groups	and	individual	interviews,	as	well	as	theory	triangulation	during	which	more	than	
one	 theoretical	 scheme	 in	 the	 interpretation	 of	 the	 phenomenon	 is	 used.	 As	 this	 research	 seeks	 to	
understand	people	and	the	social	and	cultural	contexts	within	which	they	live,	a	mainly	qualitative	approach	
to	data	gathering	was	used.	This	research	is	designed	based	on	a	mixed,	multi-method	research	approach,	
using	 both	 quantitative	 and	 qualitative	 research	 methods.	 As	 detailed	 by	 Cresswell	 &	 Clark	 (2007)	 and	
Morse	(2003)	the	premise	of	using	a	mixed	methods	research	approach	is	that	the	use	of	quantitative	and	
qualitative	approaches	in	combination	provides	a	better	understanding	of	research	problems	than	either	
approach	alone.	As	such	a	mixed	methods	research	approach	can	help	answering	questions	that	cannot	be	
answered	by	quantitative	or	qualitative	approaches	alone.	
5.1.5 Available	research	instruments	
This	research	has	been	drawing	on	the	following	triangulation	categories	proposed	by	Stake	(1995):	data	
and	 methodological	 triangulation	 by	 the	 use	 of	 multiple	 methods	 (survey,	 focus	 group	 and	 individual	
interviews)	 as	 well	 as	 theory	 triangulation.	 In	 this	 exploratory	 study,	 qualitative	 and	 quantitative	 data	
collection	 techniques	 were	 used	 and	 the	 research	 methods	 applied	 throughout	 this	 work	 consist	 of
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literature	 review,	 survey	 questionnaire,	 focus	 group	 interviews	 and	 in-depth	 individual	 interviews	 as	
depicted	within	Figures	5-1	and	5.4.		
Towards	 the	 beginning	 a	 range	 of	 potentially	 available	 methods	 was	 explored	 by	 drawing	 on	 available	
reviews	 of	 research	 methods,	 such	 as	 Creswell	 &	 Clark	 (2007)	 and	 Denzin	 &	 Lincoln	 (2002).	 Methods	
reviewed	included:		
5.1.5.1 Surveys	and	survey	questionnaires	
Surveys,	and	more	specifically	survey	questionnaires,	are	an	instrument	for	collecting	survey	information,	
providing	 structured,	 often	 numerical	 data,	 that	 can	 be	 administered	 without	 the	 presence	 of	 the	
researcher	 (Cohen,	 Manion	 &	 Morrison,	 2000:245).	 Surveys	 are	 often	 used	 to	 quantify	 or	 measure	 a	
concept.	 The	 goal	 may	 be	 to	 discover	 frequency	 of	 behaviour	 or	 to	 compare	 attitudes.	 Survey	
questionnaires	are	seen	to	be	appropriate	for	those	cases	where	the	researcher	intends	to	explore	a	topic	
by	 addressing	 a	 large	 number	 of	 people	 and	 to	 produce	 results	 that	 are	 easy	 to	 code	 and	 standardize,	
particularly	if	closed	questions,	with	a	limited	set	of	possible	responses	(Wilkinson	&	Birmingham,	2003).	
Survey	questionnaires	are	however	limited	in	order	to	provide	in-depth	and	detailed	information	and	they	
have	a	limited	scope	of	the	data	that	be	collected,	and	the	limited	flexibility	of	responses	(Cohen,	Manion	&	
Morrison,	2000:245).	
5.1.5.2 Thematic	analysis	
Thematic	analysis	is	highly	inductive,	with	the	themes	emerging	from	the	data	and	not	being	imposed	upon	
it	by	the	researcher,	(Dawson,	2002).	This	type	of	analysis	is	highly	inductive,	that	is,	the	themes	emerge	
from	the	data	and	are	not	imposed	upon	it	by	the	researcher.	In	this	type	of	analysis,	the	data	collection	
and	 analysis	 take	 place	 simultaneously.	 Even	 background	 reading	 can	 form	 part	 of	 the	 analysis	 process,	
especially	if	it	can	help	to	explain	an	emerging	theme.	Themes	then	form	the	overall	structure	for	a	content	
analysis	that	was	carried	out	manually,	using	spread-sheets,	(Litoselliti,	2003).
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5.1.5.3 Content	analysis	
Content	analysis	is	commonly	used	by	researchers	in	social	sciences	to	analyse	recorded	transcripts	and	is	
based	 on	 the	 assumption	 that	 an	 analysis	 of	 language	 in	 use	 can	 reveal	 meanings,	 priorities	 and	
understandings,	 as	 well	 as	 ways	 of	 organising	 and	 seeing	 the	 world,	 (Wilkinson	 &	 Birmingham,	 2003).”	
Often	the	message	is	delivered	as	a	text,	or	converted	to	one	(for	example,	an	interview	transcript	may	be	
produced	 or	 focus-group	 notes	 may	 be	 developed).	 In	 the	 conceptual	 analysis	 model,	 categories	 are	
developed	and	coded,	and	the	number	of	occurrences	of	themes	or	issues	is	recorded.	Content	analysis	
thus	 could	 include	 the	 study	 and	 interpretation	 of	 written	 and	 visual	 material,	 for	 example,	 magazines,	
television	advertisements,	photographs.	
5.1.5.4 Comparative	analysis	
Comparative	 analysis	 uses	 data	 from	 different	 people	 that	 is	 compared	 and	 contrasted	 in	 a	 continuing	
process	until	the	researcher	is	satisfied	that	no	new	issues	are	arising,	(Dawson,	2002).	Comparative	and	
thematic	analyses	are	often	used	in	the	same	project,	with	the	researcher	moving	backwards	and	forwards	
between	transcripts,	memos,	notes	and	the	research	literature,	(Dawson,	2002.	
5.1.5.5 In-depth	individual	interviews	
Individual	interviews	are	easier	for	the	researcher	to	control	than	a	focus	group,	in	which	participants	may	
take	the	initiative,	(Creswell	&	Clark,	2007).	Individual	interviews	are	a	purposive	sampling	method,	i.e.	a	
sample	 based	 entirely	 on	 one's	 knowledge	 of	 the	 population	 and	 the	 objectives	 of	 the	 research,	 was	
selected	as	the	most	appropriate	and	in	accordance	with	the	literature,	(Creswell	&	Clark,	2007,	Powell,	
1997).	This	is	an	understanding	shared	also	by	Leedy	&	Ormrod	(2001)	where	people,	or	other	units,	are	
chosen	for	a	particular	purpose,	implying	the	use	of	judgment	by	the	researcher.	
5.1.5.6 Telephone	interviews		
Face-to-face	interviews	are	the	most	expensive	form	of	interview.	The	interviewer	has	to	arrange	a	place	to	
hold	the	interview	and	has	to	make	the	arrangements	to	get	there	and	thus	telephone	interview	requires	
far	 less	 resources,	 (Cassiani,	 Zanetti,	 &	 Pelá,	 1992;	 Wilkinson	 &	 Birmingham,	 2003).	 However,	 a	 major
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limitation	of	telephone	interviewing	is	its	complexity	and	length	of	the	interview	since	unlike	the	dynamics	
of	face-to-face	interviewing;	it	can	be	tiresome	to	keep	the	average	person	on	the	telephone	for	longer	
than	 20–30	 minutes	 and	 all	 of	 the	 body	 language	 data	 will	 be	 lost	 using	 this	 method	 (Lavrakas,	 1993;	
Wilkinson	 &	 Birmingham,	 2003).	 In	 addition	 to	 this,	 complicated	 questions,	 and	 in	 particular	 those	 that	
require	the	respondent	to	see	or	read	something,	are	impossible	via	the	telephone;	so	they	are	perhaps	
best	 used	 for	 short	 and	 very	 focused	 interviews	 (Wilkinson	 &	 Birmingham,	 2003).	 The	 most	 common	
method	to	reduce	resistance	to	participation	has	been	to	offer	incentives	(Tourangeau,	2004).	
5.1.5.7 Grounded	theory	
Grounded	 theory	 is	 a	 form	 of	 inquiry	 used	 in	 the	 areas	 of	 education	 and	 health	 research	 where	 the	
emphasis	 is	 on	 the	 generation	 of	 theory	 that	 is	 grounded	 in	 the	 data	 and	 that	 emerged	 from	 the	 data,	
(Dawson,	2002).	This	is	different	from	other	types	of	research	that	seek	to	test	a	hypothesis.	In	grounded	
theory,	 methods	 such	 as	 focus	 groups	 and	 interviews	 tend	 to	 be	 the	 preferred	 data	 collection	 method,	
along	with	a	comprehensive	literature	review,	which	takes	place	throughout	the	data	collection	process	so	
to	help	explaining	the	emerging	results,	(Dawson,	2002).	In	grounded	theory	the	number	of	people	to	be	
interviewed	is	not	specified	at	the	beginning	of	the	research	as	the	researcher	is	open	and	responsive	to	
where	 the	 research	 will	 lead	 and	 the	 research	 and	 data	 collection	 continues	 until	 a	 saturation	 point	 is	
reached	at	which	no	new	information	is	being	collected,	(Dawson,	2002).	
• Ethnography	as	a	phenomenological	methodology	using	observed	patterns	of	human	activity	
The	 emphasis	 in	 ethnography	 is	 on	 describing	 and	 interpreting	 cultural	 behaviour	 and	 where	 the	
researchers	 immerse	 themselves	 in	 the	 lives	 and	 cultures	 that	 they	 study,	 including	 to	 live	 within	 the	
research	population	so	to	participate	in	their	activities	whilst	observing	the	populations	behaviour,	taking	
notes,	 conducting	 interviews,	 analysing,	 reflecting	 and	 writing	 reports,	 (Dawson,	 2002).	 Ethnographers	
highlight	the	importance	of	the	written	text	because	this	is	how	they	portray	the	culture	they	are	studying,	
(Dawson,	2002).
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5.1.5.8 Action	research		
Action	 research	 is	 a	 systematic	 enquiry	 with	 the	 objective	 to	 obtain	 practical	 results	 that	 allow	 for	
improving	a	specific	aspect	of	practice	and	to	make	those	results	available	for	further	scrutiny	and	testing	
(Wright,	2008).	Action	research	aims	to	deliver	practical	results	that	can	be	utilized	to	improve	or	correct	a	
current	state.	Action	research	follows	a	four	stages	cycle	(Figure	5-3)	that	emphasizes	the	importance	of	
reflection	on	action	(McMahon,	2007).	
	
Figure	5-3:	Action	Research	Cycle	(Wright,	2008).	
Action	research	is	a	deliberate	and	planned	intent	to	solve	a	particular	problem,	or	a	set	of	problems,	and	
by	 its	 nature	 involves	 strategic	 action,	 (McMahon,	 2007	 p.167).	 It	 is	 thus	 different	 to	 the	 reflective	
practitioner	model	as	expressed,	for	example,	in	Kolb’s	learning	cycle	as	going	through	the	cycle	will	not	
result	in	action	research,	(McMahon,	2007	p.167).	Action	Research	draws	on	the	interplay	of	dialogue	and	
the	 involvement	 of	 a	 group	 of	 ‘stakeholders’	 that	 are	 engaged	 in	 the	 process	 of	 inquiry	 and	 that	
collaboratively	engage	in	a	continuous	cycle	of	analysis,	reflection,	planning	and	action,	(Burns,	2006).	In	
practice	a	challenge	that	action	research	faces	is	to	establish	a	continuous	inquiry	circle,	(Burns,	2006).		
5.1.5.9 Focus	groups	
Focus	group	research	is	a	form	of	qualitative	method	used	to	gather	rich,	descriptive	data	in	a	small	group	
format	where	participants	have	agreed	to	focus	on	a	topic	of	mutual	interest	and	where	the	emphasis	is	on	
understanding	 participant’s	 experiences,	 interests,	 attitudes,	 perspectives	 and	 assumptions	 (Wilkinson	 &	
Birmingham,	2003).	Focus	groups	are	an	appropriate	means	to	explore	multiple	perspectives	of	reality	and	
how	participants	feel	and	think,	(Cole,	2006;	Morgan,	2007).	They	allow	to	explore	individual	beliefs	and	
perceptions	regarding	motivation	and	barriers	towards	the	adoption	of	more	energy	efficient	behaviour	at	
home	and	as	such	to	gain	insight	into	people’s	shared	understandings	of	everyday	life,	(Gibbs,	1997).	They
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draw	upon	respondents’	attitudes,	feelings,	beliefs,	experiences	and	reactions;	and	explore	the	role	that	
these	 individual	 beliefs,	 perceptions	 and	 social	 norms	 could	 be	 playing,	 (Gibbs,	 1997;	 Mischler,	 1986;	
Wilkinson	&	Birmingham,	2003).	The	purpose	within	the	interview	is	not	to	elicit	a	multiplicity	of	views	and	
emotional	processes	within	a	group	context,	but	rather	to	explore	on	an	individual	basis	the	meaning	and	
significance	of	what	is	happening,	(Gibbs,	1997;	Mischler,	1986;	Wilkinson	&	Birmingham,	2003).		
Focus	groups	allow	participants	to	share	their	specific	experiences	about	the	topic	under	investigation	and	
with	 those	 experiences	 being	 explored	 in	 relation	 to	 predetermined	 research	 questions,	 (Merton	 and	
Kendall,	1987).	They	thus	allow	exploring	the	everyday	use	of	language	and	culture	of	particular	groups	
(Morgan,	Krueger,	&	King,	1998;	Powell	&	Single,	1996)	so	to	produce	data	and	insight	that	would	be	less	
accessible	 without	 the	 interaction	 found	 within	 a	 group,	 (Morgan,	 1998).	 They	 allow	 for	 the	 interaction	
within	the	group	based	on	topics	that	are	supplied	by	the	researcher,	which	for	instance,	group	interviewing	
would	have	not	allowed	for,	(D.	Morgan,	1998,	p.	12).	This	allows	one	to	find	out	why	certain	topics	are	
more	 salient	 than	 others,	though	 on	 the	 downside	 there	 is	 less	 control	 over	 the	 data	 produced	 than	 in	
either	quantitative	studies	or	one-to-one	interviews,	(Morgan,	1998).	Another	possible	downside	of	focus	
groups	 is	 that	 participants	 might	 not	 be	 expressing	 their	 own	 definitive	 individual	 view,	 but	 might	 be	
influenced	by	others	in	the	group	and/or	the	group	dynamic,	(Morgan,	1998).	They	are	also	not	suitable	to	
generalize	findings	due	to	the	small	numbers	of	people	participating	and	the	likelihood	that	participants	will	
not	reflect	a	representative	sample,	(Gibbs,	1997).	
5.1.5.10 Direct	participant	observation	
Direct	observation	tends	to	be	used	in	areas	such	as	health	and	psychology	and	it	involves	the	observation	
of	 a	 ‘subject’	 in	 a	 certain	 situation,	 often	 using	 technology	 such	 as	 video,	 (Dawson,	 2002).	 Direct	
observation	is	characterized	by	a	prolonged	period	of	intense	social	interaction	between	the	researcher	and	
the	subjects,	in	the	milieu	of	the	latter,	during	which	time	data,	in	the	form	of	field	notes,	are	unobtrusively	
and	systematically	collected,	(Bogdan,	1972:3).		
Given	the	nature	of	the	research	problem	as	outlined	in	Chapter	1,	it	was	then	decided	to	adopt	a	mixed	
method	approach	as	being	the	most	appropriate	for	this	research	project	and	as	following	further	detailed.	
Each	of	the	data	collection	methods	used	in	this	research	project	could	be	considered	part	of	an	overall
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approach	to	improving	the	quality	and	validity	of	the	research	data	and	in	accordance	to	the	triangulation	
approach	 adopted.	 For	 the	 quantitative	 study	 a	 survey	 instrument	 had	 to	 be	 used	 as	 this	 was	 the	
methodology	of	choice	for	the	Energyprofiler	study	with	which	this	quantitative	part	of	the	research	had	
been	integrated.	For	the	qualitative	part	of	the	study	focus	groups	and	in-depth	interviewing	were	seen	as	
the	most	adequate	ways	to	provide	evidence	on	how	energy	is	used	at	home	in	the	context	of	people’s	
everyday	lives.	In	comparison	to	in-depth	interviewing,	focus	groups	appeared	to	have	also	an	advantage	
when	it	comes	to	observing	a	large	amount	of	interactions	in	a	limited	period	of	time.	Despite	the	potential	
disadvantage	of	telephone	interviews,	the	in-depth	interviewing	was	made	based	on	telephone	interviews	
for	logistical	reasons	and	as	existing	research	also	suggest	that	telephone	interviews	are	still	suitable	for	
short	and	very	focused	interviews	(Wilkinson	&	Birmingham,	2003),	which	had	been	the	case.	
Free	translation	was	seen	to	be	the	most	appropriate	means,	though	it	is	acknowledged	that	potentially	
other	methods	could	have	been	equally	used,	such	as	word-for-word,	literal	or	semantic	translation.	
5.2 Methods	used	
Through	 this	 research	 a	 preference	 has	 been	 given	 for	 inductive	 research,	 with	 the	 emphasis	 on	 an	
exploratory	approach	to	improve	the	understanding	of	energy	use	at	home	and	how	the	adoption	of	more	
energy	efficient	behaviour	could	be	promoted.	This	research	further	combines	positivist	and	constructivist	
paradigms,	as	use	of	both	paradigms	was	seen	to	be	an	appropriate	means	to	provide	the	researcher	with	
the	ability	to	statistically	analyse	the	data,	whilst	also	allowing	for	an	exploration	of	the	complex	set	of	
variables	that	influence	human	behaviour.	As	a	result	of	blending	such	different	approaches,	this	research	
applies	 a	 mixed,	 multi-method	 research	 methodology,	 using	 both	 quantitative	 and	 qualitative	 research	
procedures.		
As	this	research	seeks	to	understand	people	and	the	social	and	cultural	contexts	within	which	they	live,	the	
qualitative	approach	of	data	gathering	had	been	dominant	throughout	this	study.	Quantitative	research	in	
this	study	is	therefore	aimed	to	gain	insight	and	identify	issues	for	the	subsequent	qualitative	phases	of	the	
empirical	work,	while	the	qualitative	research	aims	to	explore	attitudes,	behaviour	and	experiences	through	
such	methods	as	interviews	or	focus	groups.
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Initial	 research	 was	 undertaken	 using	 secondary	 sources,	 such	 as	 published	 literature,	 discussions	 with	
other	researchers,	or	general	media	sources,	to	explore	the	overall	aim	of	the	research.	This	provided	the	
basis	for	drafting	an	initial	set	of	research	questions	and	to	deduce	from	those	a	number	of	questions	for	
inclusion	within	the	energyprofiler	study	questionnaire,	(see	section	5.3.2.	for	details).	The	energyprofiler	
study	 was	 being	 carried	 out	 in	 Portugal	 at	 the	 time	 of	 this	 research	 and	 offered	 the	 researcher	 an	
opportunity	 to	 contribute	 several	 questions	 and	 to	 access	 the	 survey	 data.	 Inclusion	 of	 data	 from	 this	
survey	was	seen	as	appropriate	to	support	the	initial	exploration	of	the	topic	under	research	and	so	to	be	
able	to	address	a	large	population	and	thus	produce	results	that	are	easy	to	code	and	standardize,	(Morgan,	
2007;	Wilkinson	 &	 Birmingham,	 2003).	Such	quantitative	approaches	are	however	limited	to	provide	in-
depth	and	detailed	information	and	thus	qualitative	methodologies	were	subsequently	used	to	explore	the	
topic	in	more	detail	and	to	allow	the	voice,	concerns	and	practices,	of	research	participants	to	be	heard,	
(Cole,	2006;	Weaver	and	Olson,	2006).	As	such,	the	initial	insight	from	the	survey	produced	an	indication	
into	the	characteristics	and	determinants	of	energy	usage	at	home,	as	well	as	the	factors	that	influence	
such.	The	objective	was	to	obtain	a	basic	understanding	of	the	subject	area,	so	to	identify	on	where	to	focus	
in	more	detail	subsequently,	to	fill	gaps	in	the	information.	
Focus	group	work	was	followed	by	individual	interviews,	which	were	considered	an	appropriate	means	to	
explore	multiple	perspectives	of	reality	and	how	participants	feel	and	think,	in	accordance	to	the	work	of	
Cole	(2006)	and	Morgan	(2007).	The	initial	focus	groups,	(see	section	5.4	for	details),	allowed	the	researcher	
to	 explore	 individual	 beliefs	 and	 perceptions	 regarding	 motivation	 and	 barriers	 towards	 the	 adoption	 of	
more	energy	efficient	behaviour	at	home	and	as	such	to	gain	insight	into	people’s	shared	understandings	of	
everyday	life,	(Gibbs,	1997).	One	objective	in	this	regard	has	been	to	draw	upon	respondents’	attitudes,	
feelings,	beliefs,	experiences	and	reactions;	focus	groups	allow	for	this.	Individual	interviews,	(see	section	
5.5	for	details),	were	then	used	to	explore	the	role	that	individual	beliefs,	perceptions	and	social	norms	
could	be	playing	in	terms	of	energy	use	and	energy	saving	on	a	day-to-day	base.	The	purpose	within	the	
interview	is	not	to	elicit	a	multiplicity	of	views	and	emotional	processes	within	a	group	context,	but	rather	
to	explore	on	an	individual	basis	the	meaning	and	significance	of	what	is	happening,	(Gibbs,	1997;	Mischler,	
1986;	Wilkinson	&	Birmingham,	2003).
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The	use	of	triangulation,	(Bergman,	2011;	Easterby-Smith	et	al.,	2002;	Golafshani,	2003;	Patton,	2002),	is	
thus	seen	to	embrace	different	aspects	of	energy	related	behaviours,	as	well	as	to	address	their	diversity	
and	complexity	so	as	to	better	understand	the	meaning	that	people	assign	to	energy	use,	exploring	the	full	
complexity	of	determinants	that	influence	energy	use,	and	to	increase	general	understanding	on	how	the	
adoption	of	more	energy	efficient	behaviours	could	be	promoted.	Triangulation	in	this	context	was	thus	
also	seen	as	a	means	to	overcome	the	influence	that	the	researcher	has	on	the	behaviour	of	participants,	or	
in	terms	of	the	bias	that	the	researcher	brings	into	the	conduct	of	the	research,	(Hussey	&	Hussey,	1997).	
Further	to	this	the	research	used	some	of	the	triangulation	categories	proposed	by	Stake	(1995),	namely	
data	 and	 methodological	 triangulation	 and	 multiple	 methods	 like	 surveys,	 focus	 groups	 and	 individual	
interviews,	 as	 well	 as	 theory	 triangulation	 during	 which	 more	 than	 one	 theoretical	 scheme	 in	 the	
interpretation	of	the	phenomenon	is	used.	
Figure	 5-4	 provides	 an	 overview	 of	 the	 research;	 namely	 literature	 review,	 survey	 questionnaire,	 focus	
group	and	in-depth	individual	interviews,	as	further	detailed	in	the	following	sections.	
	
Figure	5-4:	Research	design.	
At	the	beginning	of	the	research,	a	systematic	search	of	published	work	had	been	carried	out	so	to	gain	an	
insight	and	understanding	into	the	research	problem,	to	set	the	background	and	context	for	the	research,	
and	to	identify	gaps	in	knowledge	and	variables	to	consider	in	developing	the	key	research	questions.	With	
this,	information	was	collected	about:	(1)	the	challenge	of	sustainable	development	and	how	it	relates	to	
household	 energy	 use;	 (2)	 the	 contribution	 of	 the	 fields	 of	 economics,	 psychology	 and	 sociology	 to	
understand	human	behaviour;	(3)	the	factors	influencing	energy	use,	saving	and	conservation	at	home;	and	
(4)	the	different	alternatives	to	enable	and	promote	individual	behavioural	change.	The	literature	review	
also	included	key	academic	theories	within	the	chosen	area	and	at	a	later	stage,	it	helped	to	make	sense	of
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the	 results	 obtained	 during	 the	 different	 phases	 of	 the	 research	 by	 comparing	 the	 findings	 with	 the	
literature.		
Pre-defined	keywords	were	used	to	search	a	variety	of	on-line	available	academic	journals	and	databases.	In	
addition	 to	 this,	 bibliographies	 of	 works	 were	 examined	 so	 to	 locate	 additional	 published	 material	 that	
could	 be	 of	 interest	 to	 the	 research.	 Official	 homepages	 of	 public	 and	 private	 research	 institutes	 were	
consulted	as	well	as	personal	homepages	and	blogs	from	established	researchers	in	the	field.	Finally,	the	
outputs	 of	 national,	 European	 and	 USA	 research	 projects	 and	 newsletters	 were	 reviewed,	 such	 as	 the	
Sustainable	 Development	 Research	 Network,	 (SDRN),	 so	 as	 to	 include	 the	 latest	 research	 findings.	 The	
results	 of	 this	 literature	 review	 allowed	 for	 the	 refinement	 of	 the	 initial	 research	 questions,	 as	 well	 as	
forming	 the	 basis	 for	 the	 empirical	 part	 of	 this	 research,	 and	 for	 the	 research	 methodology	 that	 are	
presented	in	the	following.	
5.3 	Survey	questionnaire		
A	survey	questionnaire	was	used	during	the	initial	phase	of	the	research	to	gain	insight	and	identify	issues	
for	the	subsequent	qualitative	phases	of	the	empirical	work.	The	objective	in	using	this	survey	data	was	to	
explore	 key	 issues	 identified	 during	 the	 literature	 review	 and	 more	 generally,	 to	 explore	 attitudes	 and	
behaviours	to	energy	use	in	the	Portuguese	context.	The	survey	questionnaire	was	designed	and	as	part	of	
a	 wider	 study,	 the	 energyprofiler	 study,	 that	 was	 being	 carried	 out	 at	 the	 time	 of	 this	 project.	 The	
energyprofiler	study	was	a	collaborative	Portuguese	national	funded	research	project	coordinated	by	the	
author	of	this	research	on	behalf	of	Energaia,	a	local	energy	agency	in	Vila	Nova	de	Gaia,	Portugal,	together	
with	two	additional	project	partners,	Factor	Social	and	Terrasystemics.	A	number	of	questions	that	were	of	
equal	importance	to	the	energyprofiler	study	and	the	PhD	research	study	were	included	in	the	survey.	The	
researcher	was	allowed	to	reword	some	of	the	initial	energyprofiler	questions,	as	well	as	to	introduce	a	set	
of	further	questions	into	the	survey,	so	as	to	explore	issues	that	were	identified	during	the	initial	literature	
review.	These	questions	were	concerned	with	the	visibility/invisibility	of	energy	related	behaviours,	the	role	
of	 individual	 beliefs,	 motivations	 and	 perceptions	 with	 regards	 to	 energy	 use,	 and	 on	 saving	 and	
conservation	aspects,	(as	detailed	in	section	5.3.2).	The	energyprofiler	study	was	the	first	national	survey	
conducted	 in	 Portugal	 that	 collected	 data	 regarding	 individual	 perceptions,	 attitudes,	 competence	 and
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patterns	of	energy	consumption	in	the	residential	sector.	With	this	the	study	attempted	to	identify	and	
characterize	the	different	segments	within	the	Portuguese	population,	based	on	socio-psychological	and	
demographic	 factors,	 so	 to	 support	 the	 development	 of	 policies,	 programmes	 and	 interventions	 with	
regards	to	energy	efficiency	at	an	household	level,	(Energyprofiler,	2011).	
5.3.1 	Survey	questionnaire	and	data	analysis	methodology	
The	energyprofiler	study	was	based	on	telephone	interviews	with	1,019	Portuguese	inhabitants,	(aged	18+),	
that	had	been	carried	out	between	January	and	February	2010.	The	 questionnaire	 was	 designed	 by	 the	
project	 team	 with	 the	 support	 of	 an	 external	 advisor,	 Professor	 Brenda	 Boardman	 (UK),	 drawing	 on	 a	
number	of	questions	from	previous	surveys	and	it	was	refined	through	pre-testing	before	execution.	The	
representativeness	of	the	data	was	controlled	through	sample	design,	fieldwork	quotas	and	post-fieldwork	
weighting.		
Data	was	weighted	for	the	following	characteristics:	age,	gender,	area	and	sub-area.	Results	included	in	this	
thesis	 are	 based	 on	 weighted	 data	 unless	 otherwise	 stated.	 The	 survey	 data	 was	 analysed	 by	 the	
energyprofiler	project	team	using	descriptive	statistics	and	included	comparisons	of	means,	(using	t-test,	
ANOVA)	and	proportions,	(using	chi-square,	Fisher's	exact	test,	Binomial).	This	statistical	analysis	was	used	
to	characterize	individuals	regarding	their	perceptions,	attitudes,	competency,	(cognitive	and	behavioural)	
and	 their	 associated	 energy	 use	 patterns.	 The	 results	 of	 these	 analyses	 provide	 the	 data	 used	 in	 this	
research.	
The	energyprofiler	survey	questionnaire,	(Appendix	I),	included	the	following	four	groups	of	questions:		
• Group	 1;	 targeted	 at	 individual	 perceptions,	 attitudes	 and	 beliefs	 regarding	 climatic	 change,	
environmental	problems,	energy	consumption	and	energy	saving.		
• Group	2;	targeted	at	energy	consuming	behaviour,	existing	level	of	information,	competence	and	
frequency	of	specific	behaviours,	motivations	and	barriers	to	action,	as	well	as	the	usual	sources	of	
information	regarding	energy	saving	behaviour.		
• Group	 3;	 targeted	 at	 household	 characteristics,	 such	 as	 the	 type	 of	 house,	 ownership,	 type	 of	
appliances	in	the	house,	as	well	as	the	amount	of	energy	consumed.
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• Group	 4;	 targeted	 at	 the	 individual	 respondent,	 looking	 at	 characteristics	 such	 as	 age,	 gender,	
education	and	income.
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5.3.2 	Question	added	for	the	specific	purpose	of	this	research	work	
For	the	purpose	of	this	research	three	specific	additional	questions,	(Q2,	Q15	and	Q6),	were	included	in	the	
energyprofiler	questionnaire	to	provide	an	initial	insight	on	two	relevant	concepts	for	this	research:	the	
visibility/invisibility	 of	 energy	 related	 behaviours	 and	 the	 role	 that	 individual	 beliefs,	 motivations	 and	
perceptions	might	play	in	terms	of	energy	use,	saving	and	conservation	at	home.	The	three	questions	that	
were	included	were:	
• Q2:	“Which	home	appliances	do	you	have	at	home	that	consume	energy,	(think	about	gas	and	
electricity)?”	This	question	related	to	the	research	question	RQ1.	
• Q15:	“Which	reason(s)	do	you	consider	to	be	important	to	saving	energy,	(gas	and	electricity)?”	
This	question	related	to	the	research	question	RQ2.	
• Q16:	 “Why	 don’t	 you	 try	 to	 save	 energy	 more	 often?”	 This	 question	 related	 to	 the	 research	
question	RQ2.	
Q2	 was	 included	 as	 an	 open	 format	 question	 where	 people	 were	 asked	 to	 provide	 a	 list	 of	 their	 home	
appliances	 that	 consumed	 energy.	 This	 question	 was	 expected	 to	 provide	 some	 insight	 into	 those	
appliances	that	people	are	aware	of	and	also	it	might	have	been	an	indicator	for	the	energy	invisibility	of	
certain	types	or	groups	of	appliances,	as	well	as	for	energy	related	practices.		
Q15	and	Q16	aimed	to	provide	an	insight	on	individual	beliefs	with	regards	to,	(a),	individual	motivations	to	
save	energy	and	(b),	individually	perceived	barriers	to	saving	energy.	As	for	Q2,	an	open	format	was	used.	
In	 addition	 to	 those	 three	 questions	 another	 seven	 questions,	 (Q8	 to	 Q14),	 had	 been	 collaboratively	
formulated	together	with	the	energyprofiler	project	team	and	are	detailed	below.	These	questions	were	
aimed	to	explore	research	questions	RQ1	to	RQ3	in	a	broader	attempt	to	form	the	base	for	subsequent	
focus	groups	and	individual	interviews.	The	seven	questions,	(Q8	to	Q14),	are:	
• Q8	“Can	you	please	order	the	following	five	behaviours	from	the	one	that	saves	the	most	energy,	
to	the	one	that	saves	the	least?”:	the	five	behaviours	were:	1.	Reducing	shower	time	from	15	to	10	
minutes;	 2.	 Turn	 off	 equipment,	 as	 opposed	 to	 leaving	 them	 on	 "stand-by"	 mode;	 3.	 Replacing
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incandescent	 lights	 by	 fluorescent	 lights;	 4.	 Periodically	 defreeze	 freezer/fridge;	 5.	 Wash	 at	 low	
temperatures	(30-40	degree).	
• Q9	 “When	 you	 turn	 the	 heating	 on	 in	 a	 room,	 what	 do	 you	 do	 with	 regards	 to	 the	 doors	 and	
windows?”	with	a	list	of	four	possible	answers	being	provided.	
• Q10	“When	is	cold	outside,	what	do	you	do	to	increase	your	comfort	at	home?”	with	a	list	of	four	
possible	answers	being	provided.		
• Q11	“Regarding	the	fridge	and	freezer,	what	do	you	do	once	you	need	to	open	it?”	with	a	list	of	
four	possible	answers	being	provided.	
• Q12	“Regarding	the	washing	machine,	what	do	you	do	when	you	need	to	use	it?”	with	a	list	of	four	
possible	answers	being	provided.	
• Q13	“How	do	you	turn	off	the	TV	and	other	appliances?”	with	a	list	of	four	possible	answers	was	
provided.	
• Q14	 “Once	 you	 leave	 a	 room,	 what	 do	 you	 do	 with	 regard	 to	 the	 lighting?”	 with	 a	 list	 of	 four	
possible	answers	was	provided.	
Q8	 aimed	 to	 explore	 the	 existing	 level	 of	 knowledge	 regarding	 specific	 behaviours	 and	 to	 highlight	 any	
potential	gap	between	the	intent	and	impact	of	behaviour	in	terms	of	the	energy	use.	The	six	questions,	9	
to	14,	relate	to	six	specific	energy	related	behaviours	and	to	what	people	currently	do	when	facing	those	
specific	situations.	For	each	of	the	questions	a	defined	set	of	answers	was	provided	and	respondents	had	to	
choose	the	behaviour	that	they	could	identify	most	with.	The	aim	of	these	six	questions	was	to	assess	the	
behaviours	that	are	currently	being	performed	and	the	frequency	of	their	performance,	so	to	assess	the	
level	of	competence	and	performance	to	best	practice.		
The	 energyprofiler	 study	 was	 thus	 important	 to	 contextualize	 the	 topic	 of	 the	 research,	 with	 the	 initial	
findings	from	the	survey	subsequently	being	further	explored	through	the	qualitative	phase	of	this	research	
work.	The	energyprofiler	study	also	provided	some	understanding	regarding	the	motivations	to	use	and	to	
save	energy	at	home,	as	well	as	the	main	perceived	barriers	to	change	and	provided	some	answers	to	what	
enables,	explains	or	influences	energy	use	and	saving	at	home.	The	question	on	how	to	promote	different	
behaviours,	 (RQ3),	 was	 not	 addressed	 with	 the	 energyprofiler	 survey.	 The	 energyprofiler	 study	 revealed
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what	seemed	to	be	a	gap	between	existing	behaviours,	motivations	and	barriers	to	saving	energy,	which	
was	further	explored	during	the	subsequent	phases	of	the	empirical	study.	
5.4 	Focus	groups		
Focus	groups,	(FGs),	were	carried	out	with	the	aim	of	exploring	in	greater	depth	beliefs	and	perceptions	
regarding	motivations	and	barriers	towards	the	adoption	of	more	energy	efficient	behaviours	at	home.	This	
enabled	the	researcher	to	explore	the	more	general	process	of	energy	related	behaviour,	without	limiting	
the	 research	 to	 environmental	 questions,	 such	 as	 why	 individuals	 do	 not	 choose	 less	 environmentally	
damaging	and	less	energy	efficient	behaviour.	In	this	research,	focus	groups	were	used	in	a	way	similar	to	
the	work	of	Merton	and	Kendall	(1987)	by	attempting	to	get	participants	to	share	their	specific	experiences	
about	the	topic	under	investigation	and	with	those	experiences	being	explored	in	relation	to	predetermined	
research	questions.	For	the	purpose	of	this	research,	focus	groups	were	used	to	gather	insights	into,	energy	
use,	home	energy	saving	and	conservation,	to	explore	motivations,	attitudes	and	behaviours,	as	well	as	to	
prepare	the	ground	for	subsequently	conducted	interviews.	The	purpose	was	to	explore	the	everyday	use	
of	language	and	culture	of	particular	groups	as	suggested	by	Morgan,	Krueger,	&	King	(1998)	or	Powell	&	
Single	(1996).		
Instead	 of	 focus	 groups	 other	 research	 methods	 could	 have	 been	 used,	 such	 as	 direct	 participant	
observation,	group	interviewing,	or	in-depth	interviewing,	as	a	way	to	provide	evidence	on	how	energy	is	
used	 at	 home	 in	 the	 context	 of	 people’s	 everyday	 lives.	 However	 in	 comparison	 to	 direct	 participants’	
observation	 and	 in-depth	 interviewing,	 focus	 groups	 appeared	 to	 have	 an	 advantage	 when	 it	 comes	 to	
observing	a	large	amount	of	interactions	in	a	limited	period	of	time.		Since	the	FG	methodology	uses	group	
interaction	to	produce	data	and	insight	that	would	be	less	accessible	without	the	interaction	found	within	a	
group,	(Morgan,	1998).	The	focus	groups	did	provide	access	to	individuals'	interaction	on	topics	that	would	
otherwise	 have	 been	 difficult	 to	 observe,	 such	 as	 informal	 group	 conversations	 regarding	 daily	 energy	
related	behaviours,	the	determinants	of	actions	and	motivations	to	change.	In	line	with	the	literature,	the	
FGs	allowed	for,	“The	interaction	within	the	group	based	on	topics	that	are	supplied	by	the	researcher”,	
(Morgan,	1998,	p.	12),	which	for	instance,	group	interviewing	would	have	not	allowed	for.	The	Interaction	
between	participants	allowed	the	researcher	to	understand	their	view	of	the	world,	the	language	they	use
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when	discussing	energy	use,	their	values	and	beliefs,	or	the	interaction	with	participants	asking	questions	to	
each	other	so	as	to	re-evaluate	and	reconsider	their	own	understandings	of	their	specific	experiences.	This	
allowed	the	researcher	to	find	out	why	certain	topics	where	more	salient	than	others	as	the	FGs	simulate	
what	in	the	literature	is	known	as	‘a	social	gathering	and	interaction’,	(Morgan,	1998)	and	which	allowed	for	
what	seemed	to	be	multiple	interpretations	that	had	been	expressed	by	participants,	with	a	number	of	
explanations	being	provided	as	to	their	respective	behaviours.		
Focus	group	methodology	does	nonetheless	also	have	limitations.	Firstly,	there	is	less	control	over	the	data	
produced	than	in	either	quantitative	studies	or	one-to-one	interviews,	since	FG	research	is	open	ended	and	
cannot	be	entirely	predetermined,	(Morgan,	1998).	Secondly,	because	individuals	might	not	be	expressing	
their	 own	 definitive	 individual	 view,	 but	 might	 be	 influenced	 by	 others	 in	 the	 group	 and/or	 the	 group	
dynamic,	(Morgan,	1998).	Thirdly,	the	fact	that	focus	groups	are	not	suitable	for	generalizing	findings	to	a	
population,	due	to	the	small	numbers	of	people	participating	and	the	likelihood	that	participants	will	not	
reflect	a	representative	sample,	(Gibbs,	1997).	Fourthly,	the	selection	of	group	members	will	likely	affect	
the	outcome	of	the	discussion	itself,	(Wilkinson	&	Birmingham,	2003).	However,	since	the	purpose	of	this	
research	was	to	gain	a	particular	insight	into	the	topic	and	not	to	apply	generalize	findings	to	a	population,	
FGs	were	still	seen	to	be	the	most	suitable	research	method.	
5.4.1 	Focus	group	objectives	
The	objective	of	the	focus	groups	was	to	explore	a	set	of	emerging	findings	from	the	energyprofiler	study	
regarding	the	motivations	to	use	and	to	save	energy	at	home,	as	well	as	to	identify	the	main	perceived	
barriers	to	change,	(RQ2).	During	the	FGs	the	following	themes	were	explored:	
• Perceived	roles	and	functions	of	energy	use	at	home	
• Self-perception	of	own	energy	use	at	home		
• Factors	influencing	energy	use	at	home	
• Factors	that	could	facilitate	the	adoption	of	more	energy	efficient	or	related	behaviours	
FGs	were	structured	with	a	predetermined	list	of	open-ended	questions	and	activities	in	order	to	elicit	the	
constructions	and	perceptions	of	the	participants	and	without	imposing	the	researchers’	preconceptions.
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Table	5-1	presents	a	free	translation	from	Portuguese	to	English	of	the	predetermined	list	of	questions	in	
relation	to	the	objectives	and	techniques	that	were	used.	
Table	5-1	–	Focus	group	roadmap	and	techniques	used.	
Question	 Objective	 Technique	
Q1.Think	 back	 to	 yesterday.	 What	
have	you	done	that	used	energy?	
To	list	perceived	energy	consuming	
behaviours.	
Take	 people	 back	 +	 open	 question:	
write	down	on	flipchart.	
Q2.When	 you	 think	 about	 energy	
what	is	the	first	thing	that	comes	to	
your	mind?	
To	list	first	thoughts	so	to	introduce	
discussion;	expected	results:	
identified	daily	practices.	
Open	question.	
Q3.If	 energy	 was	 an	 object,	 what	
would	 be	 the	 individuals’	
characteristics?	
Evaluate	whether	people	can	picture	
energy	and	to	make	it	visible	
through	the	use	of	
adjectives/characteristics.	
Follow	up	questions	+	metaphor	and	
association;	prompt	colour,	smell,	5	
senses.	
Q4.	If	you	would	have	the	chance	to	
save	energy	why	would	you	do	so?	
Identify	motivations	to	save	energy.	
Open	question,	followed	by	probing	
and	prompting	questions	if	required.			
Q5.Think	 back	 to	 any	 attempt	 you	
made	 to	 save	 energy.	 How	 would	
you	describe	the	experience?	
Identify	individual	perceptions	once	
saving	energy,	such	as	experiences,	
motivations	or	perceived	barriers.	
Open	question.	
Q5.1.	 What	 were	 the	 reasons	 for	
such	a	success/lack	of	success?	
Follow	up	question.	
Q6.	 Some	 people	 have	 been	
reporting	difficulties	to	change	their	
energy	consuming	behaviours.	What	
is	your	personal	experience?	
Open	 question	 and	 third	 party	
projection.	
Q7.	 We	 have	 been	 hearing	 that	
people	 say	 they	 already	 save/do	 all	
they	can.	How	do	you	fell	about	it?	
Identify	perceived	barriers.	
Open	 question	 and	 third	 party	
projection.		
Q7.1.	 A	 number	 of	 reasons	 have	
been	mentioned.	I	would	like	to	ask	
you	 to	 write	 down	 the	 3	 most	
important	ones	one	per	post-it	
Follow-up	 question	 and	 group	
activity	so	to	promote	discussion	for	
grouping	those	post-its	and	label	the	
groups.	
Q7.2.	 How	 would	 you	 like	 to	 be	
helped	to	overcome	such	barriers?	
Follow-up	question.	
Q8.	Imagine	you	have	been	asked	to	
develop	 a	 future	 intervention	
program	to	be	launched	nationwide.	
What	would	you	include	within	it?	
Identify	characteristic	of	
interventions	that	were	deemed	to	
be	desired.	
Role-play;	 prompting	 for	 mediums	
to	use,	type	of	message.	
Q9.Can	 you	 share	 an	 example	 you	
recall	from	any	campaign	promoting	
energy	saving?	
Identify	initiatives	at	the	level	of	
recognition	and	recall.	
Open	question.	
Q9.1.Which	 components	 of	 the	
campaign	 have	 called	 your	
attention?	
Identify	distinctive	factors	of	
campaigns,	including	characteristics	
that	were	deemed	as	being	desired.	
Follow	up	question.	
Q9.2.	In	your	opinion	how	useful	do	
you	find	this	type	of	campaign?	
Follow	up	question.	
Q10.	Can	you	please	draw	an	image	
for	 the	 campaign,	 or	 write	 the	
slogan	you	would	use?	 To	provide	a	summary	of	the	
discussion.	
Image	 and	 word	 association,	
drawings	and	slogans	on	paper	base,	
group	activity.	
Q10.1.	 What	 was	 the	 difference	
between	this	campaign	and	the	ones	
you	have	just	been	mentioning?	
Follow	up	question.	
As	 can	 be	 seen	 from	 Table	 5-1,	 a	 variety	 of	 techniques	 have	 been	 used	 to	 promote	 the	 discussion	 and	
interaction	 between	 FG	 participants,	 but	 also	 to	 reduce	 the	 influence	 of	 the	 researcher.	 To	 generate	
practical	comparable	discussions,	a	set	of	energy	related	behaviours	were	prompted	during	the	FGs,	such	as
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showering,	lighting	and	cooking	habits,	but	also	room	temperature	and	standby	practices.	These	behaviours	
were	determined	by	considering	a	number	of	factors,	namely	their	impact	on	the	energy	bill,	their	likely	
visibility,	their	acceptability	to	the	group,	the	feasibility	of	adopting	the	behaviour	and	the	frequency	the	
behaviour	occurred.	
Within	the	FGs,	the	first	set	of	questions	explored	those	behaviours	that	were	perceived	as	energy	using	
ones,	as	well	as	the	role	and	characteristics	of	daily	energy	use.	Subsequently,	participants	were	asked	for	
motivations	 and	 barriers	 to	 saving	 energy	 at	 home	 and	 lastly	 they	 were	 asked	 for	 their	 input	 and	
perceptions	 about	 possible	 intervention	 programmes	 or	 communication	 campaigns	 to	 promote	 the	
adoption	 of	 more	 energy	 efficient	 behaviours	 at	 home.	 They	 were	 not	 specifically	 told	 that	 such	
programmes	 or	 campaigns	 must	 be	 appealing	 to	 them,	 but	 rather	 that	 it	 should	 be	 suitable	 for	 the	
population	 in	 general.	 This	 last	 part	 provided	 the	 researcher	 with	 an	 understanding	 of	 the	 kind	 of	
narratives,	focus	and	messages	that	were	perceived	to	hold	a	potential	to	promote	behavioural	change,	to	
highlight	potential	gaps	between	motivations	and	barriers	and	to	derive	from	this	a	possible	roadmap	for	
action.	
Though	this	research	is	focusing	on	day-to-day	behaviours,	discussion	also	included	investment	types	of	
decisions,	 which	 provided	 an	 insight	 into	 how	 FGs’	 participants	 understood	 the	 contribution	 to	 energy	
saving	efforts	of	both	groups	of	behaviours.	
5.4.2 	Focus	group	composition	
Results	 used	 within	 this	 research	 are	 the	 outcome	 of	 the	 seven	 FGs	 that	 took	 place	 between	 June	 and	
September	2011	in	three	different	locations	in	North	Portugal.	In	total	41	volunteers	participated	in	the	
study	 and	 this	 sample	 is	 by	 no	 means	 representative,	 though,	 an	 attempt	 had	 been	 made	 to	 provide	 a	
heterogeneous	mix	of	genders,	age,	education	and	income	levels	so	to	allow	for	a	reasonable	diversity	of	
opinions	 and	 experiences	 to	 be	 revealed.	 Therefore	 participants	 were	 selectively	 chosen	 to	 assure	 the	
desired	 level	 of	 heterogeneity.	 Variable	 gender	 was	 chosen	 over	 age	 to	 promote	 a	 dialogue	 that	 could	
underpin	specific	gender	energy	consuming	practices	at	home.	Though	any	of	these	two	variables	could	
have	been	chosen,	since	findings	from	the	energyprofiler	study	indicated	that	age,	region	and	gender	all	
seemed	 to	 influence	 the	 way	 individuals	 can	 be	 grouped	 in	 terms	 of	 energy	 use	 at	 home.	 Different
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education	 and	 income	 levels	 had	 not	 been	 a	 variable	 for	 the	 FGs’	 composition,	 though	 4	 of	 the	 FGs	
consisted	of	currently	unemployed	that	were	studying	to	obtain	high	school	equivalent	education,	while	the	
other	3	FGs	consisted	of	participants	in	regular	employment	that	held	at	least	high	school	level	education.		
When	this	research	was	initially	designed,	4	FGs	were	planned:	one	with	low	behaviour,	two	with	medium	
behaviour	and	one	with	high	behaviours	as	the	following	Figure	5-5	shows.		
	
Figure	5-5:	Initial	focus	group	design.	
The	initial	assumption	was	that	the	participants	for	the	four	focus	groups,	(Figure	5-5),	could	be	recruited	
from	 the	 group	 of	 over	 900	 people	 that	 answered	 the	 energyprofiler	 questionnaire	 and	 agreed	 to	 be	
contacted	for	follow-up	activities.	After	contacting	some	of	those	respondents,	it	became	nonetheless	clear	
that	such	recruitment	process	would	not	be	a	viable	option	because	of	geographical	distance	and	for	the	
majority	of	cases	the	inability	to	drive	long	distances.	Since	the	objective	was	to	have	face-to-face	focus	
groups	there	was	the	need	for	a	different	FG	format	to	overcome	these	barriers.	Participants	were	instead	
recruited	from	the	local	population	via	two	strategies.	Firstly	through	invitation,	(FG1,	FG2	and	FG3)	and	
secondly	by	collaborating	with	a	local	training	institute,	from	which	two	classes	of	adults	that	were	enrolled	
in	vocational	training	were	recruited,	(FG4,	FG5,	FG6	and	FG7).		
As	a	result	of	this,	a	total	of	7,	(instead	of	the	initially	4),	FGs	have	been	taking	place,	which	still	allowed	for	
the	desirable	heterogeneity.	In	addition	to	this,	this	new	approach	allowed	one	dedicated	FG	that	consisted	
of	participants	that	work	within	the	energy	efficiency	and	renewable	energy	sector	and	as	such	to	explore	
any	notable	differences	in	terms	of	behaviours,	levels	of	knowledge,	language,	and	motivations	that	could	
exist	between	expert	and	non-expert	groups.	Figure	5-6	presents	the	grouping	of	the	7	FGs.	
High	behaviour
Both	genders
Any	age
Medium	behaviour
Women
Any	age
Low	behaviour
Both	genders
Any	age
Medium	behaviour
Men
Any	age
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Figure	5-6:	Partial	and	total	distribution	of	focus	group	participants.	
At	 the	 beginning	 of	 the	 FGs,	 participants	 were	 invited	 to	 answer	 a	 simplified	 paper-based	 pre-
questionnaire,	which	was	a	reduced	version	of	the	energyprofiler	questionnaire,	(see	Appendix	II).	Based	
upon	 their	 responses	 participants	 were	 classified	 as,	 ‘low	 behaviour’	 for	 those	 performing	 none	 or	 one	
energy	 saving	 behaviour,	 ‘medium	 behaviour’	 for	 those	 performing	 between	 2	 or	 3	 energy	 saving	
behaviours,	and	‘high	behaviour’	for	those	performing	more	than	3	energy	saving	behaviours.	Figure	5-6	
shows	 the	 results	 of	 this	 questionnaire	 and	 highlights	 that	 the	 age	 group	 25-45	 might	 be	 overall	
overrepresented	but	also	that	almost	half	of	the	FGs’	participants	report	already	performing	more	than	3	
energy	saving	behaviours,	(since	they	are	classified	as	High	frequency	of	behaviour	(H)).	Participants	were	
not	given	a	financial	incentive	to	participate	in	their	FG.	
	 	
H M L H M L
<25 <25
25-45 5 25-45
>45 >45
<25 <25
25-45 1 1 25-45 2 1 2
>45 >45
H M L H M L
<25 <25
25-45 4 25-45
>45 >45 1
<25 <25
25-45 25-45 1 1 1
>45 >45 1 1
H M L H M L
<25 <25
25-45 1 25-45
>45 1 >45
<25 <25 1
25-45 25-45 1 3 2
>45 2 1 >45
H M L H M L
<25 <25 0 0 0 0
25-45 1 25-45 9 2 0 11
>45 >45 1 1 0 2
<25 1 <25 1 1 0 2
25-45 2 3 25-45 7 9 5 21
>45 >45 2 2 1 5
20 15 6 41
Frequency	of	behaviour
Male
Female
Frequency	of	behaviour
Male
Female
FG7
Frequency	of	behaviour
Male
Female
Total
Frequency	of	behaviour
Male
Female
FG5
Frequency	of	behaviour
Male
Female
FG6
Frequency	of	behaviour
Male
Female
FG3
Frequency	of	behaviour
Male
Female
FG4
FG1
Frequency	of	behaviour
Male
Female
FG2
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5.5 	In-depth	individual	interviews	
The	 information	 collected	 during	 the	 focus	 groups	 was	 subsequently	 used	 as	 the	 basis	 for	 six	 semi-
structured	in-depth	interviews:	three	with	focus	group	participants	representing	the	energy	consumers	and	
three	representing	energy	conservation	providers.	Interviews	were	semi-structured	with	a	predetermined	
list	 of	 open	 questions	 so	 to	 guide	 the	 conversation	 and	 to	 allow	 the	 participants	 to	 express	 themselves	
without	any	restriction	and	without	imposing	on	the	researchers’	preconceptions.	Individual	interviews	are	
easier	 for	 the	 researcher	 to	 control	 than	 a	 focus	 group,	 in	 which	 participants	 may	 take	 the	 initiative,	
(Creswell	&	Clark,	2007).	Other	qualitative	methods	that	had	been	considered	were	direct	observation	or	
diaries.	 Direct	 observation	 tends	 to	 be	 used	 in	 areas	 such	 as	 health	 and	 psychology	 and	 it	 involves	 the	
observation	of	a	‘subject’	in	a	certain	situation,	often	using	technology	such	as	video,	(Dawson,	2002).	For	
this	 research	 direct	 observation	 had	 been	 seen	 not	 to	 be	 suitable	 due	 to	 the	 difficulty	 of	 such	
methodologies	once	it	comes	to	observing	individual	energy	consuming	behaviours	at	home	and	within	the	
participants’	natural	settings.	Diaries	are	used	as	research	instruments	to	collect	detailed	information	about	
behaviour,	 events	 and	 other	 aspects	 of	 individuals'	 daily	 lives,	 with	 the	 narrative	 being	 built	 from	 the	
‘actors’’	point	of	view,	(Corti,	1993).	Due	to	the	number	of	energy	related	behaviours	individuals	perform	
on	daily	basis,	diaries	did	however	not	seem	to	be	a	suitable	method	of	research.	
5.5.1 	Interview	objectives	
The	in-depth	individual	interviews	built	on	the	findings	of	the	FGs,	namely	the	importance	that	individual	
beliefs,	perceptions	and	social	norms	play	in	terms	of	energy	use	and	energy	saving	on	a	day-to-day	base.	
The	 objective	 of	 the	 interviews	 was	 thus	 to	 better	 understand	 the	 individual	 motivations	 and	 barriers	
towards	the	adoption	of	more	energy	efficient	behaviours	at	home.	
	In-depth	interviews	were	used	to	explore	the	following	topics:	
• To	explore	barriers	to	adopt	more	energy	efficient	behaviours	from	a	consumer	and	a	practitioner	
point	of	view.	
• To	understand	the	meaning	of	‘comfort’,	‘convenience’	and	‘normal’	and	their	perceived	influence	
regarding	energy	use	from	a	consumer	and	a	practitioner	point	of	view.
5.	Research	methodology	and	design	
	
105	
• To	understand	whether	‘comfort’,	‘convenience’	and	‘norms’	have	been	part	of	the	considerations	
of	practitioners	when	designing	behavioural	change	interventions.	
• To	explore	different	approaches	that	could	integrate	‘comfort’,	‘convenience’	and	‘norms’	within	
behavioural	change	interventions	in	order	to	promote	a	reconsideration	of	these	at	home.	
To	generate	practically	comparable	discussions,	a	set	of	motivations,	barriers	to	action	and	energy	related	
behaviours	 sourced	 from	 the	 roundtable	 discussion	 of	 the	 focus	 groups	 were	 prompted	 during	 the	
interviews	with	energy	consumers.	Two	different	sets	of	questions	were	developed,	(see	Appendix	III	and	
IV,)	one	targeted	at	energy	consumers	and	one	targeted	at	energy	intervention	providers.	Both	groups	were	
initially	questioned	about	the	overall	degree	of	easiness	or	difficulty	to	save	energy	at	home,	as	well	as	the	
reasons	for	such	evaluation.	Energy	consumers	were	then	asked	for	their	understanding	of	‘comfort’	level	
and	‘normal’	energy	use	at	home,	about	the	impact	of	energy	saving	behaviours	and	to	identify	potential	
energy	saving	behaviours	that	they	would	be	willing	to	engage	in.	Energy	intervention	providers	were	asked	
for	their	understanding	about	what	consumers	perceived	as	level	of	‘comfort’,	‘convenience’	and	‘normal’	
energy	use	at	home.	They	were	also	asked	about	their	experience	on	behavioural	change	interventions	and	
in	 particular	 for	 those	 interventions	 focusing	 on	 promoting	 the	 adoption	 of	 a	 different	 norms	 regarding	
energy	use	at	home.	Finally	they	were	asked	about	possible	intervention	strategies	that	could	be	pursued	in	
the	future.	
5.5.2 	Sampling	of	interviewees	
A	 total	 of	 six	 interviews	 were	 performed,	 three	 with	 consumers	 and	 three	 with	 intervention	 providers.	
Considering	the	nature	of	the	research,	a	purposive	sampling	method,	i.e.	a	sample	based	entirely	on	one's	
knowledge	of	the	population	and	the	objectives	of	the	research,	was	selected	as	the	most	appropriate	and	
in	accordance	with	the	literature,	(Creswell	&	Clark,	2007,	Powell,	1997).	This	is	an	understanding	shared	
also	by	Leedy	&	Ormrod	(2001)	where	people,	or	other	units,	are	chosen	for	a	particular	purpose,	implying	
the	use	of	judgment	by	the	researcher.	Consumers	interviewees	were	selected	from	the	participants	of	the	
FGs	 based	 on	 answers	 provided	 during	 discussion	 and	 notable	 with	 regards	 to	 ‘comfort’,	 ‘convenience’,	
‘normal	consumption’	and	‘norms’.	These	topics	have	been	discussed	to	a	greater	extent	within	FG1,	FG2	
and	FG3.	Participants	of	the	other	four	FGs	were	more	concerned	with	saving	energy	as	they	could	not
5.	Research	methodology	and	design	
	
106	
afford	to	pay	higher	energy	bills	and	thus	evaluated	comfort	as	something	that	requires	money.	The	three	
consumers	interviewed	were	two	men,	(CID1	and	CID2),	and	one	woman,	(CID3).	Intervention	providers	
were	 chosen	 as	 they	 had	 been	 involved	 in	 designing	 behavioural	 change	 interventions,	 or	 as	 they	 were	
involved	in	the	policy	making	process	of	defining	the	priorities	for	national	intervention.	More	precisely	
PID1	works	in	a	department	promoting	energy	efficiency	at	one	of	the	Portuguese	energy	utility	companies.	
PID2	 works	 for	 the	 ADENE	 –	 Agência	 para	 a	 Energia,	 a	 Portuguese	 national	 energy	 agency,	 that	 is	
responsible	 for	 home	 energy	 certification,	 supporting	 the	 Portuguese	 government	 in	 the	 definition	 of	
policies	 and	 new	 legislation,	 but	 also	 managing	 a	 number	 of	 interventions	 promoting	 energy	 efficiency	
themselves.	Finally,	PID3	is	a	middle	manager	at	ERSE-	Entidade	Reguladora	dos	Serviços	Energéticos,	the	
Portuguese	 energy	 service	 regulation	 body,	 responsible	 for	 managing	 a	 Portuguese	 national	 programme	
targeted	 at	 financing	 and	 sponsoring	 behavioural	 change	 intervention	 to	 promote	 energy	 saving,	
conservation	and	efficiency	within	the	residential,	services	and	industry	sectors.	
5.6 Summary	of	empirical	study	methods	
The	previous	sections	discussed	the	main	research	methods	that	were	adopted	during	the	empirical	part	of	
this	study	and	Table	5-2	provides	an	overview	of	the	participants	for	each	of	the	three	activities	as	well	as	it	
clarifies	the	sample	and	process	for	selection	of	it.	
Table	5-2	–	Summary	of	research	activities.	
	 Survey	 Focus	Group	 In-depth	interviews	
Sample	criteria	
The	 objective	 was	 to	
have	 a	 representative	
sample	 of	 Portuguese	
citizens	from	all	regions,	
collected	 through	 quota	
sampling	 procedures,	
considering	 the	 aim	 of	
the	 study.	 The	 sample	
should	 be	 evenly	
distributed	 with	 regard	
to	 gender,	 age	 group,	
region	 and	 urban/rural	
area	(see	appendix	X	for	
detailed	 sample	
distribution).		
Participants	 were	
selectively	 chosen	 to	
assure	 the	 desired	 level	
of	 heterogeneity	 in	
terms	 of	 genders,	 age,	
education	 and	 income	
levels.		
	
A	 purposive	 sampling	
method,	 i.e.	 a	 sample	
based	 entirely	 on	 one's	
knowledge	 of	 the	
population	 and	 the	
objectives	 of	 the	
research,	was	selected.
5.	Research	methodology	and	design	
	
107	
Selection	process	
Only	one	participant	per	
household	 was	
considered	 for	
telephone	 interviews,	
performed	 by	 a	
recruitment	 and	 survey	
company	 -	 Consulmark	
(Gallup	 Group)	
nationwide.	 1019	
interviews	 were	
conducted	in	a	total.	
Participants	 were	
recruited	 from	 the	 local	
population	 via	 two	
strategies.	 Firstly	
through	invitation,	(FG1,	
FG2	 and	 FG3)	 and	
secondly	 by	
collaborating	 with	 a	
local	 training	 institute,	
from	 which	 two	 classes	
of	 adults	 that	 were	
enrolled	 in	 vocational	
training	 were	 recruited,	
(FG4,	 FG5,	 FG6	 and	
FG7).		
	
A	 total	 of	 six	 interviews	
were	 performed,	 three	
with	 consumers	 and	
three	 with	 intervention	
providers.	
5.7 	Qualitative	data	analysis:	Focus	group	and	in-depth	individual	interviews	
Focus	group	and	in-depth	individual	interviews	were	audio	recorded	and	afterwards	transcribed.	In	terms	of	
primary	qualitative	data,	a	combination	of	thematic,	comparative	and	content	analysis	was	used.	Thematic	
analysis	 was	 firstly	 used	 to	 search	 for	 keywords	 or	 concepts	 mentioned	 during	 the	 FGs	 and	 ID,	 and	 to	
identify	 overarching	 themes.	 Discussions	 of	 energy	 use	 could	 usually	 be	 found	 linked	 to	 words	 such	 as	
comfort,	convenience,	normal,	and	money	or	saving.	Thematic	analysis	is	highly	inductive,	with	the	themes	
emerging	from	the	data	and	not	being	imposed	upon	it	by	the	researcher,	(Dawson,	2002).	Drawing	from	
Litoselliti	 (2003)	 themes	 then	 formed	 the	 overall	 structure	 for	 a	 content	 analysis	 that	 was	 carried	 out	
manually,	using	spread-sheets	as	the	following	example	in	Table	5-3	demonstrates:
5.	Research	methodology	and	design	
	
108	
Table	5-3	–	Content	analysis.	
Transcript	extract	 Argumentative	categories	 Overarching	themes	
Male,	FG3:	we	cannot	separate	energy	
use	 from	 economic	 development.	 20	
years	ago	once	we	were	our	kids’	age,	
our	 country	 was	 less	 developed,	 we	
were	 a	 poorer	 country.	 Our	 parents	
could	 not	 offer	 us	 what	 we	 today	 do	
to	 our	 kids…	 The	 appeal	 to	
consumption,	with	PlayStations,	sound	
systems,	a	TV	set	in	each	room…	once	
I	was	a	child	my	parents	had	a	single	
TV	at	home,	and	nowadays	how	many	
do	we	have?	
Change	in	consumption	patterns;	
	
Change	 in	 the	 number	 of	 home	
appliances	owned;	
	
Need	to	cater	for	a	growing	number	of	
expectations	and	needs.	
Economic	 development	 as	 a	
factor	 influencing	 energy	 use	 at	
home;	
	
Number	of	owned	appliances	as	a	
factor	influencing	energy	use;	
	
Evolution	 of	 social	 norms	 as	 a	
factor	influencing	energy	use.	
Content	analysis	is	commonly	used	by	researchers	in	social	sciences	to	analyse	recorded	transcripts	and	is	
based	 on	 the	 assumption	 that	 an	 analysis	 of	 language	 in	 use	 can	 reveal	 meanings,	 priorities	 and	
understandings,	 as	 well	 as	 ways	 of	 organising	 and	 seeing	 the	 world,	 (Wilkinson	 &	 Birmingham,	 2003).	
Comparative	 analysis	 uses	 data	 from	 different	 people	 that	 is	 compared	 and	 contrasted	 in	 a	 continuing	
process	 until	 the	 researcher	 is	 satisfied	 that	 no	 new	 issues	 are	 arising,	 (Dawson,	 2002),	 and	 has	 been	
attempted	 within	 this	 research.	 Further	 to	 this,	 background	 reading	 was	 used	 as	 part	 of	 the	 analysis	
process,	in	particular	to	explain	any	emerging	theme	that	was	not	considered	in	the	initial	literature	review	
process.	The	results	of	the	qualitative	data	analysis	were	then	discussed	as	themes	and	subthemes	and	
illustrative	quotes	are	provided	throughout	this	work.	
Both	quantitative	and	qualitative	data	phases	were	conducted	in	the	Portuguese	language	with	findings	and	
analysis	translated	into	English	by	the	researcher.	Questionnaire	roadmaps,	analysis	or	illustrative	quotes	
presented	in	this	work	were	then	translated,	using	a	free	translation	style,	focusing	on	the	meaning	in	order	
to	capture	the	idea	and	context	of	what	was	said.	Other	methods	could	have	been	used,	such	as	word-for-
word,	literal	or	semantic	translation,	however	free	translation	was	seen	to	be	the	most	appropriate	means.		
5.8 	Research	ethics	
For	the	purpose	of	this	research,	primary	and	secondary	data	were	collected	to	explore	how	energy	is	used	
at	home.	The	use	of	secondary	data	is	identified	and	sources	acknowledged.	The	target	group	for	collecting	
primary	data	were	citizens	aged	18	and	above,	who	have	their	main	residence	in	Portugal.	Permission	to	
collect,	transcribe	and	to	use	the	data	for	the	purpose	of	this	research	had	been	granted	by	the	participants	
at	the	beginning	of	each	of	the	quantitative	and	qualitative	data	gathering	sessions.
5.	Research	methodology	and	design	
	
109	
In	the	case	of	the	national	survey	questionnaire,	respondents	were	chosen	randomly	through	a	professional	
company	and	they	were	informed	about	the	purpose,	methods	and	intended	possible	uses	of	the	research	
as	well	as	what	their	participation	in	the	research	entailed.	
FGs’	participants	and	ID	interviewees	participated	voluntarily	in	the	data	gathering	phases	and	no	coercion	
was	used	at	any	time	during	the	research.	FGs’	participants	and	ID	interviewees	were	informed	about	the	
purpose	of	the	research,	had	the	procedure	explained	that	would	follow	and	were	given	the	option	to	leave	
the	room	if	they	wished.	Neither	EP	respondents	nor	FGs’	participants	and	ID	interviewees	were	given	any	
type	of	compensation	for	participating	in	the	study.	Due	to	the	methodologies	used	it	is	extremely	unlikely	
there	would	be	any	direct	harm	to	the	research	participants.	No	private	and/or	sensitive	data	was	collected	
for	the	purpose	of	this	research	and	as	a	consequence	no	ethical	clearance	was	required	from	the	OUUK.	
Once	conducting	the	focus	groups	and	interviews,	commonly	accepted	techniques	were	used	and	special	
attention	 was	 paid	 to	 the	 design,	 revision	 and	 undertaking	 so	 to	 ensure	 integrity	 and	 quality.	 The	
confidentiality	of	information	supplied	by	participants,	and	the	anonymity	of	respondents,	was	respected	
and	 guaranteed	 due	 to	 the	 use	 of	 codes	 to	 represent	 FG	 participants	 and	 interviewees.	 Further,	 audio	
recordings	 and	 transcripts	 of	 the	 focus	 groups	 and	 interviews	 were	 kept	 confidential	 and	 in	 a	 secure	
location.	 No	 image	 that	 would	 allow	 visual	 identification	 was	 made	 during	 any	 of	 the	 phases	 of	 the	
empirical	study.	Collected	primary	data	from	the	survey	questionnaire	was	computed	by	the	energyprofiler	
project	team	using	SPSS,	with	the	researcher	being	directly	involved	during	the	pre	and	post	analysis	of	the	
data.	 This	 research	 uses	 the	 results	 of	 such	 analysis	 and	 no	 further	 analysis	 of	 data	 was	 performed.	
Qualitative	 data	 was	 analysed	 using	 commonly	 accepted	 analytical	 techniques,	 with	 a	 combination	 of	
thematic,	comparative	and	content	analysis	used.	
5.9 	Summary	
This	chapter	explains	the	various	options	available	during	the	field	research	part	of	this	study	and	the	logic	
for	the	selection	of	the	specific	approach,	strategy	and	methods,	some	of	which	required	a	more	subjective	
approach	due	to	the	nature	of	collecting,	analysing	and	interpreting	the	more	qualitative	focus	group	and	
interview	data.	In	summary	the	research	is	mainly	of	an	inductive	nature	in	terms	of	formulating	a	theory
5.	Research	methodology	and	design	
	
110	
from	 bottom-up,	 and	 using	 a	 multi-method	 approach	 that	 combines	 a	 survey,	 with	 focus	 groups	 and	
individual	in-depth	interviews	as	the	primary	research	methods.
6.	Exploring	domestic	energy	use	
	
111	
6 	Exploring	domestic	energy	use		
Chapters	 6,	 7	 and	 8	 present	 and	 discuss	 the	 findings	 from	 the	 empirical	 work	 as	 outlined	 in	 Chapter	 5;	
namely	from	the	energyprofiler	survey	questionnaire,	((EP),	see	5.3),	the	Focus	Groups,	((FG),	see	5.4)	and	
from	in-depth	individual	interviews,	((ID),	see	5.4).	Individual	interviews	involved	consumers,	(CID),	as	well	
as	intervention	providers,	(PID).	The	objective	of	using	data	from	the	EP	was	to	set	the	broader	context	of	
the	research,	with	the	FGs	and	ID	interviews	exploring	specific	topics	that	emerged	from	the	EP	findings.	
The	relationship	between	chapters	6,	7	and	8,	and	the	research	questions	is	shown	subsequently	in	Table	6-
1.		
Table	6-1	–	Relation	in	between	chapter	and	research	questions.	
Chapter	 RQs	
Chapter	6	 RQ1:	What	explains	energy	use	at	home?	
Chapter	7	 RQ2:	What	influences	energy	use	at	home?	
Chapter	8	 RQ3:	What	is	the	potential	role	of	intervention	strategies	on	energy	use	at	home?	
6.1 	Characteristics	of	domestic	energy	use	
The	characteristics	of	energy	use	were	explored	in	all	stages	of	the	research	and	two	main	characteristics	
emerged	during	the	empirical	study:	the	invisibility	of	energy	in	home	and	the	fundamental	role	that	it	plays	
on	day-to-day	practices.	
6.1.1 	Invisibility	as	a	distinctive	characteristic	of	energy	use		
During	 the	 FGs	 and	 ID	 interviews,	 energy	 was	 often	 reported	 as	 invisible,	 in	 particular	 referencing	
electricity.	In	fact,	some	of	the	FGs’	participants	said	that	utilities	such	as	water	or	gas	were	less	abstract	to	
them	than	electricity,	as	one	FG	participant	summarized:	
“For	instance	with	electricity	I	think	it	is	more	difficult	because	it's	something	one	can't	see.	
With	a	water	tap	open	one	can	see	the	amount	of	water	flowing”,	Female,	FG3
6.	Exploring	domestic	energy	use	
	
112	
A	few	FGs’	participants	expressed	this	invisibility	by	comparing	energy	use	with	the	purchase	of	goods	and	
how	less	visible,	intangible	and	more	immaterial	the	purchase	of	energy	can	be:	
“Because	energy,	one	does	not	buy	in	packages,	(comparing	it	to	the	purchase	of	goods	at	a	
supermarket)”,	Female,	FG6	
Given	the	overall	agreement	among	FGs’	participants	that	energy	and	in	particular,	electricity,	is	something	
invisible	 and	 immaterial,	 the	 topic	 was	 not	 further	 prompted	 during	 the	 ID	 interviews.	 During	 CID,	
interviewees	did	not	establish	this	relationship	by	themselves;	whilst,	contrary,	it	was	brought	up	by	PID	
interviewees,	 who	 frequently	 discussed	 how	 invisibility	 could	 increase	 the	 difficulty	 of	 promoting	 more	
energy	 efficient	 behaviours.	 This	 indicates	 a	 different	 level	 of	 awareness	 between	 consumers	 and	
intervention	providers.		
On	a	day-to-day	basis	energy	was	reported	as	visible	through	a	number	of	ways.	During	FGs,	participants	
discussed	their	interaction	with	energy	namely,	(1),	through	the	services	and	amenities	energy	provides	for	
their	 home	 appliances,	 or,	 enrolling	 in	 practices,	 such	 as	 cooking,	 lighting,	 or	 washing	 for	 example;	 (2),	
when	 purchasing	 home	 appliances,	 as	 a	 moment	 in	 time	 where	 energy	 use	 was	 considered	 within	 the	
purchase	process;	(3),	when	paying	energy	bills,	or	buying	bottled	gas,	or	wood;	this	action	reminded	them	
of	their	energy	use.		
As	a	starting	point	to	exploring	the	question	during	the	EP	survey	questionnaire,	respondents	were	asked,	in	
an	open-format	type	of	question	without	being	prompted,	to	name	all	the	energy-consuming	appliances	
they	 owned	 at	 home.	 This	 question	 was	 aimed	 at	 understanding	 the	 respondent’s	 perception	 regarding	
those	home	appliances	that	consumed	energy.	An	assumption	in	asking	this	question	was	that	there	would	
be	a	body	of	un-reported	home	appliances,	as	respondents	either	do	not	have	those	appliances,	or	because	
they	do	not	recall	having	them	as	they	did	not	associate	such	appliances	with	energy	consumption,	(i.e.	
insignificant	 or	 invisible	 energy	 consumption),	 (Energyprofiler,	 2011).	 To	 exclude	 the	 possibility	 of	 non-
existent	 equipment,	 the	 EP	 team	 compared	 the	 findings	 of	 the	 EP	 survey	 questionnaire	 with	 the	
penetration	 rate	 of	 such	 appliances	 within	 the	 Portuguese	 population,	 using	 the	 latest	 available	 data
13
.	
																																																																				
13
	"Household	Expenditure	Survey"	(2005-2006	-	INE)
6.	Exploring	domestic	energy	use	
	
113	
Figure	 6-1	 compares	 the	 difference	 between	 the	 numbers	 of	 home	 appliances	 EP	 respondents	 reported	
owning,	(here	presented	in	percentage)	and	National	reported	figures.	
	
Figure	6-1:	Percentages	of	home	appliances	reported	by	EP	respondents	[n=1.014]	in	comparison	to	national	
ownership	data,	(Energyprofiler,	2011).	
Based	on	the	findings	illustrated	in	Figure	6-1,	the	EP	team	concluded	that	there	appeared	to	be	a	gap	
between	 reported	 and	 owned	 home	 appliances,	 (Energyprofiler,	 2011).	 EP	 findings	 indicate	 that	
respondents	may	have	not	reported	some	appliances	and	tend	to	underestimate,	mainly,	the	smaller	and	
technology/entertainment	related	appliances.	The	only	exception	to	this	is	the	cooker,	which	was	the	main	
underestimated	large	appliance.	An	explanation	for	this	might	be,	that	in	Portugal	cookers	are	frequently	
run	on	gas	and	not	electricity,	and	that	gas	is,	perhaps,	not	understood	as	being	an	energy	source.	With	
regards	to	underestimating	small	and	technology/entertainment	related	appliances,	one	interpretation	for	
this	 is	 that	 EP	 respondents	 have	 those	 appliances	 at	 home,	 but	 forgot	 to	 report	 them,	 due	 to	 their	
perceived	insignificant	energy	consumption.	From	the	data	presented	in	Figure	6-1,	this	cannot	be	clearly	
concluded,	therefore	this	matter	was	further	explored	during	FGs	by	asking	participants	to	report	how	they	
used	energy	at	home	the	previous	day.	This	question	provided	an	extensive	list	of	answers	as	summarized	
in	Figure	6-2.
6.	Exploring	domestic	energy	use	
	
114	
	
Figure	6-2:	Reported	home	appliances	and	practices	during	FGs	once	participants	were	asked	what	they	did	the	day	
before.	
As	 can	 be	 seen	 in	 Figure	 6-2,	 the	 list	 of	 reported	 home	 appliances	 and	 practices	 is	 extensive	 and	
comprehensive,	and	do	not	support	the	assumption	that	EP	respondents	might	have	forgotten	to	report	
home	 appliances	 based	 on	 low	 energy	 consumption.	 From	 the	 findings	 of	 the	FGs’	 participants	 it	 is	 not	
possible	 to	 conclude	 for	 or	 against	 any	 predominant	 reason.	 However,	 FG	 interactions	 seemed	 to	 have	
facilitated	a	recalling	of	a	more	comprehensive	list	of	home	appliances,	as	well	as	the	respective	practices.	
This	suggests	that	during	the	EP	survey,	respondents	might	have	simply	forgotten	to	recall	some	of	the	
home	appliances	that	they	owned.	One	such	reason	for	forgetting	home	appliances	could	be	simply	not	
having	recent	interaction	with	the	appliance	or	associated	practices,	and	as	the	following	quote	indicates:	
“Usually	I	will	use	the	washing	machine	each	second	day”,	Female	FG6	
A	further	reason	for	not	reporting	appliances	and	practices	has	been	an,	apparent,	underreporting	of	
those	which	people	do	not	need	to	interact	with	in	terms	of	‘switching	on	or	off’:	
“W1:	we	are	talking	about	the	lights	but	there	are	other	things	that	are	always	on	like	the	
fridge.	W2:	yes,	I	was	excluding	those	things”,	FG2	
It	 could	 further	 be	 observed,	 that	 the	 moment	 of	 purchase	 served	 as	 a	 reminder	 to	 a	 few	 of	 the	 FGs’	
participants	and	CID	interviewees	as	to	how	much	energy	they	use	at	home.	Thus,	it	could	be	seen	as	a	
moment	 in	 time	 when	 energy	 appears	 to	 have	 a	 higher	 visibility,	 through	 product	 energy	 labelling	 for	
Practices
Lights Entertainment	appliances Lighting
TV Stove Doing	the	laundry
PC Fridge Doing	the	dishes
Microwave Freezer Cooking
Iron Radio Prepare	some	toasts
Microwave	watch Light	and	engine	of	the	aquarium Listening	to	music
Standby	lights Water	engine Ironing
Washing	machine Electrical	gates Charge	mobile
Hoover Drill Charge	camera
Exhaust	fan Playstation Watching	TV
Tumble	dryer Gas	for	shower Charge	tooth	brush
Presence	light	for	kids Coffee	machine Showering
Boiler Fan
Television	set Battery	of	mobile	phone
Hot	water Hair	dryer
Heat	pump	to	heat	water Vacuum	cleaner
Coffee	machine Small	appliances
Hand-blender All	other	appliances	that	are	on	24h
Home	appliances
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example,	with	narratives	during	the	discussions	suggesting	a	period	of	reflection	before	the	purchase	of	
such	appliances.	Overall,	FGs’	participants	reported	considering	different	alternatives	when	buying	home	
appliances,	as	well	as	being	more	aware	of	energy	efficient	items;	but,	that	those	might	not	be	the	final	
purchase,	as	the	following	quote	summarizes:	
“I	 think	 we	 don't	 pay	 much	 attention	 to	 A-class	 appliances	 which	 allow	 you	 to	 use	 less	
energy.	 However,	 once	 we	 are	 looking	 for	 buying	 an	 home	 appliances	 there	 is	 a	 big	
difference	in	price”,	Female,	FG6	
The	 quote	 above,	 also	 highlights	 that	 the	 purchase	 decision	 process	 embraces	 not	 only	 the	 amount	 of	
energy	 the	 appliance	 will	 use	 but	 also	 the	 investment	 required	 in	 buying	 more	 energy	 efficient	 ones,	 a	
phenomenon	 that	 research	 to	 date	 has	 identified	 as	 a	 barrier	 to	 the	 purchase	 of	 more	 energy	 efficient	
appliances,	as	well	as	the	adoption	of	renewable	energy	sources,	(Barenergy,	2011;	Gardner	&	Stern,	2002,	
2008;	Jackson,	2005).	From	the	findings	of	the	FGs	and	the	ID	interviews,	it	was	not	possible	to	understand	
whether	 purchasing	 more	 energy	 efficient	 home	 appliances	 accounted	 for	 the	 majority,	 or	 not,	 of	 the	
purchasing	decisions,	but	that	the	purchase	itself	might	indeed	provide	energy	with	some	visibility.	
In	addition	to	this,	energy	bills	were	considered	by	the	majority	of	FGs’	participants	and	CID	interviewees	as	
a	moment	in	time	when	energy	appears	to	gain	some	visibility.	It	remained,	however,	unclear	as	to	how	far	
energy	bills	actually	contributed	to	energy	visibility.	FGs’	participants	prevalent	feelings	was	that	energy	
bills	provided	little	helpful	information,	in	terms	of	the	amount	of	energy	being	used,	which	suggests	that	
energy	 bills	 in	 Portugal	 might	 be	 obscuring	 rather	 than	 helping	 understanding	 of	 their	 energy	 use.	 FGs’	
participants	provided	a	number	of	reasons	for	this:	(1),	energy	bills	are	usually	sent	out	bi-monthly	and	
often	 report	 on	 estimated	 energy	 consumption,	 rather	 than	 real	 consumption	 levels;	 (2),	 Not	 all	 energy	
sources	are	accounted	for	through	the	energy	bill.	FGs’	participants	seem	to	overlook	energy	sources	that	
were	not	accounted	for	in	the	energy	bill,	such	as	bottled	gas	and	firewood.	FGs’	participants	seemed	to	
have	difficulties	in	estimating	their	monthly	use	of	bottled	gas	and	firewood;	(3),	The	fact	that	a	significant	
number	 of	 FGs’	 participants	 reported	 paying	 a	 fixed	 amount	 during	 11	 months	 of	 the	 year	 with	 the	
difference	 being	 paid	 in	 the	 12
th
	 month.	 Thus,	 this	 contributes	 to	 a	 lack	 of	 understanding	 of	 energy	
consumption	on	a	monthly	base,	as	the	following	quote	illustrates:
6.	Exploring	domestic	energy	use	
	
116	
“I	pay	the	same	amount	each	month	and	only	at	the	end	of	the	year	I	pay	the	difference	of	
the	energy	use.	It's	very	difficult	to	know	how	much	energy	I	used	during	the	months”	Male,	
FG3	
The	12
th
	month	energy	bill	was,	apparently,	a	subject	of	close	reflection	for	a	significant	number	of	FGs’	
participants	and	CID	interviewees;	(4),	Pay	bills	using	direct	debit,	was	reported	to	contribute	towards	the	
increased	invisibility	of	energy	use;	(5),	Portuguese	energy	bills	also	include	surcharges,	that	are	not	related	
to	energy	use	and	that	could	account	for	up	to	44.9	percent	of	the	final	price	for	electricity,	(Eurostat,	n.d.),	
that	 could	 hinder	 understanding	 how	 much	 energy	 is	 used.	 Some,	 but	 not	 all,	 of	 these	 surcharges	 are	
disclaimed	 within	 the	 bill,	 which	 contributes	 to	 a	 lack	 of	 transparency.	 Commonly,	 the	 above	 reasons	
question	the	efficacy	of	energy	bills	in	the	one	form	or	another	to	provide	an	adequate	level	of	information.	
6.1.2 	The	fundamental	role	of	domestic	energy	use		
The	FG	discussions	and	the	CID	interviews	showed	strong	agreement	in	the	fundamental	role	that	energy	
plays	for	people,	as	the	following	quote	summarizes:	
“Electricity	allows	us	to	use	our	five	senses,	by	seeing	TV,	listening	to	music,	(…),	also	the	smell	
with	a	freshener,	(…),	to	cook…,(not	finishing	to	go	through	the	remaining	senses)”	Female	
FG2	
FGs’	 participants	 and	 CID	 interviewees	 agreed	 that	 energy	 is	 fundamental	 to	 fulfil	 basic	 needs,	 such	 as	
cooking	or	bathing,	but	also	aspects	that	belonged	to	normal	needs	and	lifestyles	and	related	to	comfort,	
convenience	or	common	practices.	With	this,	some	of	the	FGs’	participants	also	expressed	some	frustration	
that	they	could	not	fulfil	all	their	needs	without	having	to	worry	about	the	next	energy	bill,	since	energy	was	
too	costly	to	fulfil	all	their	needs.	As	such	there	was	an	overall	agreement	among	FGs’	participants	and	CID	
interviewees	regarding	energy	as	fundamental,	vital	or	essential.	
6.2 	Determinants	of	domestic	energy	use	
Energy	use	at	home	is	often	explained	as	based	on	a	set	of	factors	and	existing	conditions,	(EEA,	2013;	
Maréchal,	2010)	and	this	section	aims	to	explore	such	factors	and	conditions	that	had	been	reported	during
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the	empirical	study	and	to	reflect	on	determinants	that	are	influencing	home	energy	usage.	The	results	for	
this	section	are	given	as	a	series	of	themes	that	emerged	during	the	FGs	and	the	ID	interviews,	as	FGs’	
participants	and	ID	interviewees	had	not	been	directly	asked	for	what	determines	their	energy	use	at	home.	
6.2.1 	Relation	of	behaviour	and	energy	use	
Findings	from	the	EP	survey,	FGs	and	CID	interviews	indicate	that	people	have	already	adopted	some	more	
energy	 efficient	 behaviours.	 Q6	 of	 the	 EP	 survey	 questionnaire,	 an	 open-ended	 question,	 asked	
respondents	to	explain	what	they	were	already	doing	to	save	energy	at	home.	EP	respondents	were	invited	
to	provide	a	list	of	everything	they	did	to	save	energy	and	as	the	resulting	data	is	presented	in	terms	of	the	
frequency	of	answers	in	relation	to	the	total	amount	of	respondents.	As	Figure	6-3	shows,	the	responses	
provided	by	the	EP	survey	included	a	range	of	efficiency	and	curtailment	behaviours,	(Appendix	V	provides	
a	full	list	of	answers).	
	
Figure	6-3:	Reported	energy	efficient	behaviours,	in	percent	of	total	No.	of	respondents	[n=1.014]	(Energyprofiler,	
2011).	
0,0% 10,0% 20,0% 30,0% 40,0% 50,0% 60,0% 70,0%
Bought	a	smaller	fridge
The	thermostat	is	at	a	maximum	of	18	°	Celsius
Double	glasses
Insulation	of	the	house
I	don’t	use	the	pre-wash	step	in	the	dishwasher
Have	solar	panels	at	home	(thermal/photovoltaic)
Insulation	of	doors	and	windows
Energy	efficient	heating	system
Turn	off	the	central	heating	during	the	summer
Energy	class	A	appliances
Always	use	the	washing	machine/dishwasher	completely	full
Cook	with	gas
Hand	wash	the	dishes
Turn	down	the	washing	machine/dishwasher	temperature
Air	dry	the	clothes
Take	a	quick	shower
Others
Use	of	efficient	lamps
Turn	off	appliances	(and	don’t	leave	them	on	stand-by)
Turn	off	the	lights	when	there	is	no	one	in	the	room
0,3%
0,4%
0,6%
0,7%
0,8%
1,2%
1,5%
1,7%
3,5%
8,2%
9,2%
10,3%
11,4%
11,6%
12,2%
13,8%
20,2%
34,4%
44,0%
61,7%
Energy	efficient	behaviours
6.	Exploring	domestic	energy	use	
	
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The	results,	as	presented	in	Figure	6-3,	show	that	the	most	commonly	adopted	behaviours	are	curtailment	
behaviours	 of	 turning	 lights	 off	 and	 avoiding	 standby	 consumption.	 These	 curtailment	 behaviours	 are	
followed	by	the	purchase	of	energy	efficient	light	bulbs	and	home	appliances,	(energy	class	A	appliances	in	
Figure	6-3).	In	contrast	to	this,	efficiency	behaviours	related	to	water	and	space	heating	were	less	reported.		
	
Figure	6-4:	Frequency	of	reported	energy	saving	behaviours	in	FG	pre-questionnaire.	
Figure	6-4	shows	the	results	of	the	FG	pre-questionnaire,	(see	Appendix	II	for	the	full	version	of	the	pre-
questionnaire)	and	as	can	be	seen	34	out	of	41	FGs’	participants	reported	to	use	energy	efficient	light	bulbs,	
followed	by	25	participants	using	A	class	or	more	energy	efficient	appliances,	17	participants	controlling	
room	temperature	and	14	insulating	their	doors	and	windows.	Equally,	during	the	FG	discussions	and	CID	
interviews,	the	purchase	of	energy	efficient	light	bulbs	and	home	appliances,	as	well	as	turning	lights	off	
and	avoiding	standby,	had	been	reported	as	the	most	widespread	efficiency	and	curtailment	behaviours.	
These	 four	 behaviours	 could,	 during	 the	 discussion,	 be	 traced	 back	 to	 past	 nationwide	 interventions	 in	
which	energy	efficient	light	bulbs	had	been	provided	for	free,	or	discounts	offered	for	more	energy	efficient	
major	home	appliances.	The	four	energy	saving	behaviours	most	often	cited	in	the	pre-questionnaire	might,
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however,	be	the	result	of	a	bias,	since	they	were	already	provided	as	options	to	answers	for	Question	2	in	
the	same	questionnaire.	Since	controlling	room	temperature	and	insulating	doors	and	windows,	had	a	high	
response	 rate	 in	 the	 pre-questionnaire,	 it	 only	 was	 discussed	 within	 the	 FGs	 once	 prompted.	 Thus,	 the	
reported	behaviour	appeared	to	not	correspond	to	the	actual,	current,	behaviour.	However,	the	fact	that	
the	FGs	took	place	during	summer,	when	such	behaviours	are	not	performed,	might	have	been	an	equally	
valid	explanation	and	from	observations	this	remains	unclear.	
A	 second	 set	 of	 questions,	 (Q9	 to	 Q14),	 in	 the	 EP	 survey	 questionnaire	 further	 explored	 the	 level	 of	
adoption	of	best	practice,	in	terms	of	energy	efficient	behaviour,	in	six	specific	situations,	as	can	be	found	in	
Table	6-2.	
Table	6	-2	–	Reported	energy	efficient	behaviours	[n=1.014],	(Energyprofiler,	2011).	
Specific	Situation	(by	survey	
question)	
Reported	results	
Question	 9	 –	 “When	 you	
turn	 on	 the	 heating	 system	
in	a	room,	how	do	you	leave	
the	windows	or	doors?”	
22.2	 percent	 of	 respondents	 reported	 the	 adoption	 of	 best	 practice	 by	 answering	
that	 they	 not	 only	 close	 doors	 and	 windows,	 but	 additionally	 they	 insulated	 the	
house	to	prevent	heat	losses.	Most	respondents,	(38.8	percent),	closed	doors	and	
windows,	 without	 thermally	 insulating	 the	 house.	 Only	 about	 4	 percent	 of	
respondents	did	nothing,	or	only	close	windows/doors	once	they	remember.	
Question	 10	 –	 “When	 it’s	
cold	outside	what	do	you	do	
to	 enhance	 the	 comfort	 at	
home?”	
42.8	percent	of	respondents	reported	the	adoption	of	best	practice	by	first	putting	
on	extra	clothes	and	then	increasing	room	temperature	if	necessary.	Only	about	5.6	
percent	of	respondents	seek	high	thermal	comfort	without	worrying	about	energy	
conservation.	A	large	percentage,	represented	mainly	in	"other"	procedures,	have	
no	electric	heating	or	fireplace	and	thus,	don’t	fit	in	this	question.	
Question	11	–	“What	do	you	
do	 once	 you	 open	 the	
fridge/freezer?”	
65.5	percent	of	respondents	reported	the	adoption	of	best	practice	by	trying	to	close	
the	door	as	quickly	as	possible	and	remove	everything	they	need	at	once.	Only	about	
5	 percent	 of	 respondents	 did	 not	 indicate	 concerns	 about	 energy	 conservation	
related	to	fridge	usage.	
Question	12	–	“What	do	you	
do	 once	 using	 the	 washing	
machine?”	
75.8	percent	of	respondents	reported	adoption	of	the	best	practice	by	always	using	
the	washing	machine	at	maximum	load	and	air	drying	their	clothes.	Only	about	8	
percent	of	respondents	did	not	indicate	concerns	about	energy	conservation	at	this	
level.	
Question	13	–	“How	do	you	
turn	 off	 the	 TV	 and	 other	
appliances?”	
64	 percent	 of	 respondents	 reported	 the	 adoption	 of	 best	 practice	 by	 turning	
appliances	off.	Still,	a	high	percentage	of	respondents,	(24.2	percent),	reported	using	
the	stand-by	option	of	the	equipment.	Only	about	11	percent	of	respondents	did	not	
indicate	concerns	about	energy	conservation	at	this	level,	never	shutting	off	or	doing	
it	once	they	remember.	
Question	 14	 –	 “When	 you	
leave	 a	 room	 what	 do	 you	
do	in	relation	to	the	lights?”	
About	 86.8	 percent	 of	 respondents	 reported	 the	 adoption	 of	 best	 practice	 by	
reporting	that,	"As	a	rule,	I	turn	off	the	lights	when	I	leave	a	room".	Only	about	3	
percent	of	respondents	did	not	indicate	concerns	about	energy	conservation	at	this	
level,	never	turning	off	the	light	or	only	doing	so	once	they	remember.	
The	responses	shown	in	Table	6-2	indicate	a	good	level	of	knowledge	and	adoption	of	more	energy	efficient	
behaviours	 regarding	 lighting	 and	 stand-by	 practices.	 Nevertheless,	 when	 it	 comes	 to	 other	 behaviours,	
such	as	interaction	with	major	home	appliances,	home	thermal	insulation	or	showering	practices,	this	level
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of	reported	knowledge	and	adoption	of	energy	efficient	behaviour,	is	less	often	reported	which	indicates	it	
might	also	be	less	often	adopted.		
From	the	above	findings,	in	combination	with	the	FG	discussions	and	interview	responses,	the	following	
could	be	learnt.	Firstly,	the	energy	efficiency	of	appliances	does	not,	on	its	own,	appear	to	necessarily	be	a	
guarantee	of	lower	energy	use,	since	it	is	the	way	that	people	use	their	appliances	that	influences	actual	
energy	 consumption.	 This	 point	 will	 be	 discussed	 more	 in	 section	 6.2.3	 and	 is	 supported	 by	 literature,	
(Goldblatt,	2005;	INE,	I.P./DGEG,	2011;	Lomas,	2010).		The	responses	of	FGs’	participants	and	CID	interviews	
indicated	that	there,	indeed,	seemed	to	be	a	dissonance	between	the	behaviour	of	purchasing	an	appliance	
in	relation	to	its	use.	For	example,	a	significant	number	of	FGs’	participants	reported	buying	energy	efficient	
light	bulbs,	whilst	at	the	same	time	paying	less	attention	to	the	way	they	used	the	lamp,	as	exemplified	
within	the	following	quote:	
“That's	the	reason	why	they	developed	the	energy	efficient	light	bulbs.	They	know	we	will	not	
switch	lights	off”,	Male,	FG7	
This	suggests	that,	despite	technological	developments	and	the	use	of	more	energy	efficient	appliances,	
energy	intense	habits	might	still	be	maintained	and	therefore	potential	energy	gains	could	be	lost.	This	is	
described	 in	 literature	 as	 the,	 “Rebound	 effect”,	 (Khazzoom,	 1980)	 and	 as	 illustrated	 in	 the	 quote,	 as	 a	
direct	rebound	effect.	Findings	further	show	that	reported	energy	saving	behaviour	frequently	focused	on	
easy	to	perform	behaviours	that	have	no	apparent	impact	in	terms	of	comfort,	convenience	and	wellbeing	
such	as	the	one	expressed	in	the	quote	above.	These	findings	should,	however,	be	evaluated	with	care	for	
two	reasons.	Firstly,	it	was	not	always	clear	whether	FGs’	participants	and	ID	interviewees	were	influenced	
by	 what	 they	 perceived	 the	 researcher	 wanted	 to	 have	 as	 an	 answer,	 or,	 whether	 the	 responses	 are	 a	
consequence	 of	 participants	 wanting	 to	 maintain	 a	 consistency	 in	 their	 own	 reasoning,	 which	 from	 the	
literature	is	influenced	by	the,	“Cognitive	dissonance	theory”,	(Festinger,	1957).	Secondly,	energy	seems	to	
be	strongly	associated	with	electricity	and	seen	as	a	synonym	for	electricity,	or	perhaps	for	electricity	plus	
gas.	Therefore	responses	might	well	be	limited	equally	to	such	energy	sources	only.
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6.2.2 	Building	characteristics		
The	 majority	 of	 the	 FGs’	 participants	 and	 ID	 interviewees	 seemed	 to	 understand	 the	 role	 building	
characteristics	 have	 with	 regards	 to	 the	 amount	 of	 energy	 used	 on	 a	 day	 to	 day	 basis,	 as	 well	 as	 the	
limitation	 that	 they	 represent	 to	 adopt	 energy	 efficient	 behaviour.	 Building	 characteristics	 discussed	
included	age,	orientation,	size,	building	envelope,	performance	of	installed	heating/cooling	system,	as	well	
as	 the	 potential	 to	 refurbish,	 or	 install	 renewable	 energy	 systems.	 Situations,	 such	 as	 not	 being	 able	 to	
reduce	 energy	 use	 due	 to	 lock-in	 effects,	 were	 reported	 by	 all	 6	 ID	 interviewees	 and	 by	 a	 few	 FGs’	
participants,	as	the	following	quotes	demonstrate:	
“There	are	already	a	number	of	technical	solutions	within	building	options	that	could	protect	
the	environment	that,	due	to	the	fact	of	being	so	expensive,	are	not	often	used”,	Male,	FG3	
“If	we	want	to	install	a	solar	panel	they	are	so	expensive”,	Female	FG6	
Two	 of	 the	 PID	 interviewees	 further	 considered	 building	 characteristics	 to	 be	 a	 strong	 determinant	 for	
domestic	energy	use	and	that	other	factors,	such	as	location	or	style	preferences,	were	of	a	higher,	decision	
making,	importance	than	energy	efficiency	when	purchasing	property.	PID1	argued	that	only	a	small	niche	
of	the	population	seemed	to	take	the	energy	efficiency	of	their	new	homes	into	consideration.	Given	that	
ownership	of	a	house	was	not	a	segmentation	criterion	for	selecting	FGs’	participants	and	CID	interviewees,	
it	was	not	possible	to	understand	whether	the	energy	efficiency	of	new	homes	was	a	variable	in	the	house	
selection	process.	
6.2.3 	Growing	number	of	home	appliances	
A	number	of	FGs’	participants	and	CID	interviewees	further	acknowledged	that	they	own	a	growing	number	
of	 appliances	 in	 comparison	 to	 the	 past.	 By	 the	 past,	 they	 were	 usually	 referring	 to	 what	 their	 parents	
owned	at	that	age,	or	when	they	were	younger	and	still	lived	with	their	parents.	However,	no	relationship	
was	established	by	them	between	technological	efficiency	gains	per	appliance,	the	overall	growing	number	
of	appliances,	and	the	impact	that	this	could	have	on	the	amount	of	energy	being	used.	As	a	result	of	this	
and,	apart	from	two	cases,	FGs’	participants	and	CID	interviewees	did	not	seem	to	be	aware	of	the	impact	
of	the	growing	number	of	home	appliances	and	related	higher	energy	consumption.	This	phenomenon	is
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discussed,	 within	 research,	 as	 one	 of	 the	 explanations	 for	 the,	 “Energy	 efficiency	 gap”,	 (Feenstra	 et	 al.,	
2009)	and	the	PID	interviewees	supported	this.	
Though	 not	 understanding	 the	 full	 scope	 of	 the	 increased	 number	 of	 appliances	 they	 owned,	 FGs’	
participants	provide	a	number	of	examples	of	this	evolution	of	ownerships,	such	as	increased	numbers	of	
TV	 sets	 per	 household,	 the	 change	 from	 washing	 clothes	 by	 hand	 towards	 a	 washing	 machine,	 or	 the	
growing	penetration	rate	of	heating/cooling	systems.	
“I	have	an	AC	at	my	holiday	house	that	I	use	to	heat	during	winter	and	cool	during	summer.	
For	sure	afterwards	I	need	to	pay	the	bill,	but	it	feels	good.	Maybe	15	years	ago	I	didn't	have	
an	AC	and	I	survived”,	Female,	FG2	
The	quote	above	not	only	shows	that	some	of	the	FGs’	participants	started	to	own	home	appliances	they	
were	not	used	to	owning,	but	that	this	can	also	represent	an	evolution	of	needs	and	expectations,	as	a	
combination	of	comfort	and	affordance.	
Heating	systems,	both	water	and	room,	were	also	a	part	of	the	discussion	among	all	7	FGs.	In	general,	FGs’	
participants	seemed	to	be	aware	of	the	impact	that	such	home	appliance	can	have	in	terms	of	contribution	
to	electricity	and/or	gas	bill.	Nevertheless,	in	three	FGs,	one	misconception	was	often	observed	in	regard	to	
the	belief	that	one	is	saving	energy	by	using	wood,	instead	of	gas	or	electricity.	FGs’	participants	seemed	to	
believe	they	were	saving	energy	without	recognizing	they	were	simply	exchanging	one	energy	source	for	
another.	Only	one	FG	participant	mentioned	that	the	energy	efficiency	of	their	heating	system	had	been	a	
discussion	point	once	building	their	house.	
6.2.4 	Energy	efficient	home	appliances	and	overall	energy	prices	
Findings	 from	 the	 EP	 survey	 show	 that	 energy	 consumption	 was	 reported	 as	 the	 most	 important	
characteristic,	(31.1	percent),	when	deciding	to	purchase	electrical	appliances.	This	is	followed	by	energy	
labels
14
,	with	29.2	percent.	Lower	percentages	include	the	price/quality	ratio,	(17.8	percent),	price,	(16.8	
percent),	 or	 power,	 (e.g.	 watts),	 (14.3	 percent).	 However,	 those	 findings	 should	 be	 analysed	 with	 some	
																																																																				
14
	According	to	the	European	Union	Energy	Label	Standard.
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caution	since	they	are	not	in-line	with	other	research	in	this	area	that	shows	a	different	order	of	purchasing	
factor	priorities,	with	quality	being	first,	followed	by	price	and	only	then	comes	energy	consumption,	as	
presented	within	the	results	of	the	energyprofiler	study,	(Energyprofiler,	2011).	One	of	the	reasons	for	such	
a	result	might	be	that	people	were	questioned	about	the	main	characteristics	of	their	home	appliances	that	
they	bought	the	year	before,	within	a	survey	that	related	to	energy	use.	This	could	have	triggered	energy	
consumption	as	the	first	answer.	This	apparent	contradiction	could	also	be	observed	within	the	responses	
of	some	of	the	FGs’	participants	and	ID	interviewees:			
“I	think	we	don't	pay	much	attention	to	A-class	appliances	which	allow	you	to	use	less	energy.	
However,	once	we	are	deciding	to	buy	an	home	appliances	there	is	a	big	difference	in	price”,	
Female,	FG6	
The	findings	from	the	FGs	and	ID	interviewees	did	not	also	provide	any	clear	evidence	on	how	relevant	
energy	use	can	be	when	purchasing	a	home	appliance.	FGs’	participants	and	CID	interviewees,	however,	
identified	higher	purchasing	prices	as	a	barrier	to	the	purchase	of	more	energy	efficient	appliances,	since	
this	would	require,	–	inter-alia		–	investing	up-front	with	savings	benefits	only	achievable	in	the	medium-
long	term:		
“The	price	difference	of	A-class	appliances	is	considerably	more	expensive	which	is	a	reason	
for	not	buying	such	class	of	appliances”,	Female,	FG6	
During	the	FGs	and	the	CID	interviews,	it	was	not	possible	to	fully	understand	whether	participants	were,	
indeed,	 purchasing	 energy	 efficient	 home	 appliances,	 or	 whether	 their	 monetary	 situation	 presented	 a	
limitation	 to	 such	 purchases.	 Evidence	 was	 provided	 for	 both	 cases,	 both	 buying	 more	 energy	 efficient	
appliances	and	also	for	being	unable	to	afford	them,	even	though	they	were	aware	of	the	benefits:	
“I'm	proud	of	having	a	heat	pump	at	home	since	it	was	sold	as	being	a	very	efficient	solution	
to	heat	water…this	makes	me	feeling	happy	with	my	decision”,	Female,	FG2	
In	order	to	fully	understand	the	impact	of	the	higher	price	of	energy	efficient	appliances,	in	terms	of	energy	
use	at	home,	requires	understanding	how	the	costs	of	running	such	an	appliance	could	compare	to	the
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initial	investment	required.	This	is,	in	particular,	meaningful	since	saving	money	had	been	reported	as	the	
main	motivation	to	save	energy	at	home,	during	the	energyprofiler	survey	and	one	could	expect	that	any	
change	in	energy	prices,	be	it	in	absolute	or	relative,	would	influence	consumption.	However,	this	is	not	
always	the	case	and	during	the	empirical	work	evidence	was	provided	that	challenged	this	assumption.	
During	the	FGs	stage,	two	categories	of	participants	were	identified.	Firstly	a	group	that	appeared	to	be	
able	to	afford	higher	energy	bills	and,	secondly,	a	group	that	reported	to	have	a	limited	amount	of	money	
to	spend	on	energy.	Participants	belonging	to	the	first	group	seemed	to	be	aware	of	the	need	of	saving	
energy	and	reported	trying	to	do	so.	However,	they	also	reported	to	be	willing	to	spend	a	higher	amount	on	
energy,	 in	 order	 to	 maintain	 their	 desired	 level	 of	 comfort	 at	 home,	 which	 suggests	 that	 concepts	 of	
comfort	and	perceived	needs	might	increase	with	income	level.	The	second	group	included	participants	that	
reported	reducing	their	energy	use,	to	the	minimum	required,	in	order	to	fulfil	what	they	perceived	as	basic	
needs,	with	some	of	those	participants	reporting	that	they	could	not	afford	services	and	amenities,	such	as	
room	heating	during	winter,	as	they	would	have	liked	to.	For	this	second	group,	using	more	energy	was	
reported	as	not	being	a	viable	option	because	they	simply	could	not	afford	it.	This	group	of,	what	seemed	to	
be,	less	affluent	FGs’	participants	might	even	be	in	an	energy	or	fuel	poverty	situation	as	during	the	FGs,	a	
significant	number	of	participants	from	FG4,	5,	6	and	7	reported	experiences	that	appear	to	be	situations	of	
energy	and/or	fuel	poverty.	Yet,	there	was	an	overall	agreement	among	these	less	affluent	FGs’	participants	
to	aspire	to	lifestyles	which	lead	to	the	adoption	of	more	energy	inefficient	behaviours.	Within	this,	they	
could	be	considered	frugal	consumers	who	are	obliged	to	keep	costs	down.	
The	discussions	also	showed	a	consensus	among	FGs’	participants	that,	if	the	price	for	energy	was	lower,	or	
they	 could	 have	 more	 money	 to	 spend,	 (meaning	 the	 relative	 price	 of	 energy	 was	 reduced),	 this	 would	
result	in	them	using	more	energy:	
“The	reason	for	reporting	to	save	is	a	monetary	one,	perhaps	if	they	had	more	money	they	
would	use	more	energy”,	(reporting	on	how	she	perceived	others	motivation	to	save	energy),	
Female,	FG4	
“Depends	on	the	individual	financial	circumstances:	those	spending	more	money	on	energy	
can	afford	doing	so	(…)	they	can	pay	more	and	save	less”,	Male,	FG4
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These	quotes	indicate	a	possible	relationship,	not	only	between	decreasing	price	and	higher	energy	use,	but	
also	 of	 increasing	 income	 levels	 and	 increasing	 energy	 use	 and	 that	 energy	 use	 would	 almost	 certainly	
increase	if	FGs’	participants	either	had	more	money	to	spend,	or	if	energy	prices	decreased,	making	energy	
relatively	cheaper.	On	the	other	side,	if	energy	price	did	go	up,	this	might	not	impact	energy	use	that	much	
in	the	short-term.	Those,	more	frugal,	FGs’	participants	appeared	to,	perhaps,	not	manage	to	save	energy	as	
they	 already	 only	 use	 it	 for,	 perceived,	 basic	 needs.	 Some,	 more	 affluent	 FGs’	 participants,	 in	 contrary	
appeared	to	not	have	such	constraints.	These	findings	provide	further	evidence,	supporting	the	literature	
regarding	 energy	 use,	 as	 inelastic	 in	 the	 short	 term,	 but	 more	 elastic	 in	 the	 long	 term,	 as	 suggested	 by	
Sorrell	(2007).	This	suggests	that	only	at	a	certain	price	could	one	expect	to	see	a	reduction	on	energy	use.	
Other,	more	affluent,	FGs’	participants	pointed	out,	however,	that	if	they	could	afford	to	pay	higher	energy	
bills,	they	also	would	be	doing	so.	This	provides	evidence	supporting	the	body	of	literature	that	advocates	
that	higher	income	might	lead	to	higher	energy	use,	(DECC,	2011;	Gatersleben	et	al.,	2002).		
These	 findings	 nevertheless	 raise	 a	 question	 regarding	 the	 effectiveness	 of	 those	 types	 of	 interventions	
targeted	at	changing	energy	prices.	During	the	FGs,	a	number	of	such	intervention	types	were	discussed,	
such	as	taxes	or	subsidies,	with	subsidies	being	favoured	by	participants	over	taxes.	Within	five	of	the	seven	
FGs	a	type	of	intervention	was	discussed	that	aimed	at	penalizing	bad	behaviours,	(i.e.	energy	overuse),	
providing	some	further	incentive	for	the	good	behaviour,	(i.e.	energy	underuse).	A	significant	number	of	
FGs’	participants	were	receptive	to	the	position	of	paying	a	penalty,	which	could	be	an	increased	energy	
price,	 compared	 to	 the	 standard	 price.	 Similarly,	 in	 those	 cases	 where	 energy	 was	 underused,	 FGs’	
participants	 suggested	 a	 bonus	 for	 good	 performance.	 Nevertheless,	 the	 initial	 enthusiasm	 of	 FGs’	
participants	towards	such	type	of	intervention	and	the	effectiveness	of	the	intervention	was	not	clearly	
established.	In	light	of	the	discussion	of	the	previous	paragraph	the	validity	of	these	responses	is,	perhaps,	
not	entirely	clear.	
6.2.5 	The	evolution	of	cultural	and	social	norms	
Institutional,	 social	 and	 cultural	 factors	 influence	 the	 way	 lives	 are	 lived	 based	 on	 the	 norms	 that	 are	
established.	During	the	FGs	and	ID	interviews,	a	common	theme	related	to	the	evolution	of	standards	of	
comfort,	namely	thermal	comfort,	or	convenience	of	newly	established	practices,	which	were	considered	by
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FGs’	 participants	 and	 ID	 interviewees	 to	 be	 a	 mix	 between	 individual	 preferences	 and	 social/cultural	
common	understandings.	FGs’	participants	provided	a	number	of	examples	for	practices	that	have	been	
evolving	over	time,	as	for	instance	heating	or	doing	their	laundry	and	dishes	and	how	a	new	way	of	doing	
these	 has	 developed	 that	 was	 expected	 to	 be	 followed.	 This	 evolution	 seem	 to	 be	 the	 result	 of	 the	
interaction	between	the	introduction	of	home	appliances,	the	ability	to	operate	them	and	what	has	become	
a	normal	way	of	doing	these	activities,	as	one	of	the	FGs’	participants	summarized	it:	
“I	 don’t	 know	 how	 I	 could	 live	 without	 my	 washing	 machine.	 I	 know	 in	 older	 times	 people	
didn’t	had	one	but	nowadays…I	mean	I	do	know	how	to	wash	clothes	by	hand	but	just	the	idea	
of	the	cold	water…”,	Female,	FG4	
The	quote	expresses	not	only	how	people	seemed	to	have	adapted	new	practices	at	home,	but	also	how	
these	new	ways	might	lock	individuals	into	these	new	practices,	creating	a	dependency	on	a	day-to-day	
basis,	with	individuals	finding	it	hard	to	change	their	domestic	routines	and	behaviours.	This	is	to	say	that	
the	 evolution	 in	 the	 number	 of	 appliances	 and	 associated	 practices	 seemed	 to	 be	 accompanied	 by	 an	
evolution	of	individual	needs	and	aspirations	that	become	normal:	
“We	got	used	to	the	comfort,	to	have	all	lights,	to	see	TV,	we	got	used	to	all	of	this.	That	does	
not	mean	that	if	someone	would	take	all	of	that	away	we	would	not	survive.”	Female,	FG7	
A	question,	therefore,	was	whether	FGs’	participants	and	ID	interviewees	perceived	these	home	appliances	
already	as	a	basic	need,	or	whether	they	were	still	considered	as	being	a	luxury.	During	the	FGs	and	ID	
interviews,	a	number	of	participants	and	interviewees	acknowledged	that	some	home	appliances	and	daily	
practices	could	be	perceived	as	a	luxury,	based	on	the	comfort	level	they	were	associated	with.	This	was	
particularly	evident	when	discussing	shower	practices	and	room	temperature	during	winter.	During	the	FGs,	
participants	provided	some	examples	of	appliances	that	they	considered	to	be	fundamental	for	their	day-
to-day	lives,	namely	the	fridge,	the	washing	machine,	lights	and	the	stove,	due	to	the	essential	role	that	
they	play	within	daily	routines.	This	dichotomy	between	basic	and	luxury	need	was	explored	in	more	detail	
during	the	CID	interviews	by	asking	interviewees	if	they	were	to	reduce	their	energy	use	what	would	they	
consider	as	a	basic	need	and	what	would	they	consider	a	luxury.	CID	interviewees	experienced	difficulty	in	
clearly	separating	basic	needs	from	luxury	and	it	appeared	that	basic	needs	were	understood	as	everything
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they	currently	do,	meaning	nothing	would	be	considered	a	luxury	for	them.	As	such,	basic	needs	included	a	
reasonable	room	temperature,	a	reasonable	amount	of	light	and	the	required	number	of	showers	to	feel	
clean.	The	definition	of	‘reasonable’	has	never	been	specified	in	detail,	but	rather	remains	as	an	abstract	
concept	of	having	a	brighter	or	warmer	house.	Luxury	needs	that	hold	a	saving	potential	were	reported	in	
some	 areas,	 such	 as	 reducing	 shower	 duration,	 avoiding	 standby	 consumption,	 avoiding	 leaving	 on	
unnecessary	lights	and	appliances,	which	could	all	be	considered	as	avoiding	energy	waste.	This	suggests	
that,	overall,	FGs’	participants	and	CID	interviewees	appeared	to	be	aware	of	what	good	practices	are	under	
specific	situations.	However,	they	did	not	perceive	non-performance	of	good	practice	as	being	a	luxury.	
Findings	indicated,	however,	that	knowing	about	good	practice	did	not	translate	into	concrete	behaviour	
and,	 particularly,	 when	 comfort	 seemed	 to	 be	 a	 dominant	 need	 that	 is	 both	 socially	 aspired	 for	 and	
accepted.	From	the	FGs	and	CID	interviews	no	consistent	narrative	emerged	of	a	moral	obligation	to	use	
energy	in	a	different	way.		
6.3 	Concluding	remarks	
This	chapter	discussed	the	findings	from	the	empirical	study	that	looked	at	how	energy	is	used	at	home	in	
terms	of	its	characteristics	and	determinants	within	the	Portuguese	context.	Table	6.3	provides	an	overview	
about	the	findings,	how	those	relate	to	the	research	questions	and	any	noteworthy	observations,	followed	
by	a	summary	of	the	findings	with	regards	on	how	they	relate	to	the	first	research	question,	(RQ1)	and	the	
literature.
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Table	6-3	–	Summary	of	findings	relating	to	RQ1	
Empirical	study	findings	 RQ	 Noteworthy	further	observation	
Chapter	Section:	6.1.	Characteristics	of	domestic	energy	use	
6.1.1.	Invisibility	as	a	distinctive	characteristic	of	energy	use	
Energy	appears	to	be	generally	seen	as	an	abstract	concept	as	a	result	
of	its	invisibility.	
RQ1a	
Apparent	gap	between	reported	and	owned	home	appliances,	notably	for	the	case	of	small	
and	entertainment	appliances.	
Energy	 being	 visible,	 (1),	 through	 the	 services	 and	 amenities	 it	
provides	 once	 using	 home	 appliances	 and	 developing	 practices,	 (2),	
once	 paying	 for	 energy	 bills	 and,	 (3),	 once	 purchasing	 home	
appliances,	as	this	constitutes	a	moment	of	reflection	where	different	
alternative	appliances	are	compared.	
RQ1a,	RQ1c	
Scope	of	association	between	home	appliance	and	associated	practice	and	corresponding	
energy	use	remained	unclear.	
Unclear	understanding	of	the	final	purchasing	decision:	is	it	for	or	against	energy	efficient	
appliances?	
6.1.2.	Domestic	energy	use	as	being	fundamental	
Energy	to	be	seen	as	being	essential	for	people	to	live	the	way	they	
know	 and,	 in	 particular,	 to	 support	 what	 is	 seen	 as	 their	 normal	
lifestyle	that	not	only	fulfils	the	basic	needs	of	water,	food	and	shelter,	
but	also	perceived	needs	of	comfort	and	convenience.	
RQ1c	 		
Energy	 is	 perceived	 as	 something	 rare	 and	 expensive,	 resulting	 in	 a	
need	 to	 save	 energy	 at	 home;	 in	 opposition	 with	 the	 preference	 to	
fulfil	individual	needs	without	any	limitations,	or	concerns.	
RQ1c	
Findings	 indicate	 a	 strong	 association	 of	 energy	 to	 electricity	 than	 to	 any	 other	 energy	
source.	A	reason	for	this	might	be	the	fact	that	electricity	is	the	main	energy	source	for	
domestic	energy	use	in	Portugal.
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Empirical	study	findings	 RQ	 Noteworthy	further	observation	
Chapter	Section:	6.2.	Determinants	of	domestic	energy	use	
6.2.1.	Relation	of	behaviour	and	energy	use	
The	 energy	 efficiency	 of	 appliances	 alone	 is	 not	 necessarily	 a	
guarantee	of	less	energy	being	used,	since	the	way	people	use	their	
appliances	equally	influences	actual	consumption.	
RQ1b	 		
Focus	 on	 easy	 to	 do	 behaviours,	 with	 reduced	 impact	 in	 terms	 of	
comfort,	convenience	and	wellbeing.	
RQ1b	
Turning	 lights	 off	 and	 avoiding	 standby	 consumption	 as	 the	 most	 often	 reported	
curtailment	behaviours.		Purchasing	energy	efficient	light	bulbs,	as	well	as	energy	efficient	
home	appliances,	is	reported	as	the	most	widespread	efficiency	behaviour.	In	contrary	to	
this	efficiency,	behaviours	related	to	water	and	space	heating,	were	less	often	reported.	
6.2.2.	Building	characteristics	
Individual	choices	are	constrained	and	shaped	by	the	socio-technical	
system,	this	is	the	homes	they	live	in	and	the	appliances	they	own.	
RQ1b	 		
6.2.3.A	growing	number	of	home	appliances	
Evidence	 of	 the	 growing	 number	 of	 energy	 using	 appliances	 to	 be	
found	in	the	average	home.	
RQ1b	 		
6.2.4.	Energy	efficient	home	appliances	and	overall	energy	prices	
Despite	 the	 increased	 energy	 efficiency	 of	 homes	 and	 appliances,	
there	has	been	an	increase	in	domestic	energy	use,	which	could	be,	for	
example,	 a	 result	 of	 the	 way	 appliances	 are	 used	 as	 well	 as	 the	
rebound	effect.	
RQ1b	
Unclear	 understanding	 of	 the	 importance	 that	 Portuguese	 people	 attribute	 to	 energy	
consumption	of	home	appliances	at	the	moment	of	purchase.	Within	the	energyprofiler	
study	energy	consumption	was	considered	to	be	the	most	important	aspect,	despite	there	
had	been	equally	contradicting	findings	within	the	same	study,	(Energyprofiler,	2011).	Also	
through	the	subsequent	FGs	and	CID	interviews	no	clear	evidence	could	be	collected.
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Empirical	study	findings	 RQ	 Noteworthy	further	observation	
6.2.4.	Energy	efficient	home	appliances	and	overall	energy	prices	(cont.)	
Energy	use	as	price	inelastic	in	the	short	term	but	seen	to	be	elastic	in	
the	long	term.	
RQ1b,	RQ1c	 		
Unclear	 relation	 between	 income	 level	 and	 energy	 use,	 through	 an	
observed	tendency	for	higher	reported	income	levels	to	be	associated	
with	higher	reported	energy	use.	
RQ1b,	RQ1c	 		
Evidence	of	energy	and	fuel	poverty	as	a	social	and	material	problem.	 RQ1b,	RQ1c	 		
6.2.5.	The	evolution	of	cultural	and	social	norms	
Needs	developed	over	time,	referring	to	basic	requirements	of	water,	
food	 and	 shelter,	 as	 well	 as	 socially	 perceived	 needs	 of	 comfort,	 or	
convenience.	 All	 of	 these	 are	 perceived	 as	 belonging	 to	 a	 normal	
lifestyle,	with	evidence	of	comfort	and	convenience	as	socially	framed	
needs	or	wants	as	custom	within	society.	
RQ1b,	RQ1c	
Apparent	social	and	cultural	needs	of	owning	more	and	more	home	appliances,	behaving	in	
a	way	that	could	be	considered	energy	intensive	and	favouring	the	maintenance	of	comfort	
levels.	A	general	tendency	of	understanding	comfort	and	convenience	as	needs	that	must	
be	fulfilled,	but	not	as	luxury	needs.	Being	able	to	fulfil	these	needs	appears	to	be	socially	
and	culturally	accepted	and	almost	desirable.	
Social	 and	 cultural	 factors	 influence	 the	 way	 lives	 are	 lived	 once	
practices	have	been	established,	with	standards	locking	people	into,	
what	then,	appear	to	be	normal	social	practices.	
RQ1b,	RQ1c	
For	 the	 Portuguese,	 house	 heating	 has	 a	 lower	 share	 of	 total	 energy	 consumption	
compared	 to	 European	 values,	 (70	 percent	 on	 an	 average),	 which	 may	 be	 the	 result	 of	
milder	climatic	conditions,	in	combination	with	fuel	poverty	(Backhaus	et	al.,	2012;	BPIE,	
2011).	
More	 affluent	 people	 appear	 to	 trade	 money	 for	 comfort	 and	
convenience,	giving	priority	to	individual	and	family	wellbeing,	rather	
than,	 for	 instance,	 environmental	 protection.	 Those	 in	 apparent	
energy	and	fuel	poverty	seemed	to	not	be	able	to	reach	an	aspired	
comfort	 level	 and	 in	 some	 cases	 they	 might	 even	 live	 in	 unhealthy	
conditions.	
RQ1b,	RQ1c	
Most	energy,	in	Portugal,	is	spent	on	house	heating,	in	the	kitchen	and	on	water,	though	
less	evidence	exists	for	Portugal,	regarding	the	way	people	consume	energy	in	their	homes,	
as	well	as	behaviours	which	hold	the	highest	energy	saving	potential.
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Empirical	study	findings	 RQ	 Noteworthy	further	observation	
6.2.5.	The	evolution	of	cultural	and	social	norms	(cont.)	
Behaviours	 appeared	 to	 be	 socially	 determined	 by	 norms,	 by	 what	
others	around	do	and	by	copying	the	way	that	others	around	behave.	
This	 seemed	 to	 be,	 in	 particular,	 true	 once	 these	 behaviours	 had	
become	routine.	
RQ1b,	RQ1c	 		
There	is	little	evidence	that	norms	could	help	promoting	more	energy	
efficient	behaviours.		
RQ1b,	RQ1c
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The	following	summary	provides	evidence	on	how	the	findings	reported	in	this	chapter	provide	answers	to	
the	research	questions	1,	(RQ1),	what	explains	energy	use	at	home	and	the	sub-questions,	(RQ1a),	what	are	
the	 characteristics	 of	 energy	 use	 at	 home,	 (RQ1b),	 what	 are	 determinants	 of	 energy	 use	 at	 home	 and	
(RQ1c),	how	do	individuals	understand	their	energy	use.		
With	regards	to	RQ1a	and	the	characteristics	of	energy	use	at	home,	two	characteristics	emerged.	First,	the	
invisibility	 of	 energy	 has	 been	 perceived	 as	 a	 distinctive	 characteristic	 of	 energy	 use.	 Findings	 provide	
further	 evidence	 that	 energy	 is	 perceived	 as	 something	 invisible	 that,	 compared	 to	 other	 utilities,	 is	
intangible	and	abstract.	Improving	energy	visibility	was	seen	as	a	means	to	promote	and	foster	the	adoption	
of	more	energy	efficient	behaviours,	though	FGs’	participants	and	CID	interviewees	equally	showed	that	
even	 once	 visible,	 they	 had	 little	 knowledge	 about	 how	 much	 energy	 they	 use,	 both	 of	 which	 are	 well	
known	from	literature,	(Brandon	and	Lewis,	1999;	Darby,	2006;	Goldblatt,	2005;	Martiskainen,	2007).	A	well	
discussed	example,	the	energy	bill,	showed	that	despite	making	energy	visible	the	impact	is	limited	and	the	
empirical	 study	 seems	 to	 confirm	 the	 findings	 of	 Darby	 (2006)	 and	 Brandon	 and	 Lewis	 (1999).	 FGs’	
participants	 prevalent	 feeling	 was	 that	 energy	 bills	 provided	 little	 helpful	 information,	 in	 terms	 of	 the	
amount	of	energy	being	used	at	home,	which	suggests	that	energy	bills	might	obscure,	rather	than	help,	
understanding	of	energy	use.	Their	efficacy	to	provide	an	adequate	level	of	information,	that	could	support	
a	comprehensive	evaluation	of	energy	use	at	home,	was	also	questioned,	as	highlight	by	Darby	(2006)	and	
Brandon	and	Lewis	(1999).	In	addition	to	this,	from	the	findings	of	FGs	and	the	ID	interviews,	it	was	not	
possible	to	clearly	understand	whether	when	reporting	on	energy	use,	FGs’	participants	and	ID	interviewees	
only	talked	about	electricity,	or	if	they	also	referred	to	other	energy	sources,	such	as	gas	or	firewood.	Such	
a	difference	might	be,	however,	of	particular	importance	since	findings	have	equally	shown	that	energy	as	a	
concept	holds	a	stronger	association	to	electricity,	than	to	any	other	type	of	energy	source.	Therefore,	it	
might	be	assumed	that	participants	might	have	understood	energy	as	being	synonymous	with	electricity.		
The	second	emerging	characteristic	of	energy,	(RQ1a),	relates	to	the	fundamental	role	energy	plays	in	day	
to	 day	 life,	 a	 characteristic	 that	 was	 not	 challenged	 during	 the	 FGs	 and	 the	 CID	 interviews	 and	 which,	
indeed,	 is	 very	 much	 in	 line	 with	 the	 literature,	 (Geller	 et	 al.,	 2006;	 OECD,	 2012;	 Sorrell,	 2007).	 This	
characteristic,	 strongly	 related	 to	 the	 way	 individuals	 understand	 their	 energy	 use,	 (RQ1c),	 as	 this	
fundamental	 role	 appears	 to	 be	 mediated	 by	 the	 needs	 that	 it	 fulfils,	 including	 those	 that	 result	 from
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existing	lifestyles.	Such	needs	in	the	majority	related	to	comfort,	convenience	and	wellbeing,	practices	that	
become	habitual	and	thus	perceived	as	being	normal	needs.	This	seems	to	match	well	with	findings	from	
literature	 and	 that	 suggests	 that	 concepts	 of	 comfort	 and	 perceived	 needs	 might	 increase	 with	 income	
level;	an	assumption	supported	by	earlier	research,	(WWF,	2012;	DECC,	2011;	Gatersleben	et	al.,	2002).	
Findings	 further	 show	 that	 reported	 energy	 saving	 behaviour	 frequently	 focused	 on	 easy	 to	 perform	
behaviours	 that	 have	 no	 apparent	 impact	 in	 terms	 of	 comfort,	 convenience	 and	 wellbeing.	 The	 strong	
dependency	and	reliance	on	energy	might	also	explain	why	energy	was	perceived	as	expensive	by	FG	and	ID	
participants.	This	is	to	say	that	FGs’	participants	and	ID	interviewees	appeared	to	be	quite	comfortable	with	
a	certain	level	of	normalization,	where	individual	energy	use	is	perceived	and	evaluated	as	normal,	even	
though	 it	 was	 understood	 as	 being	 energy	 intensive.	 This	 observation	 supports	 findings	 from	 literature,	
(Bandura,	1977b,	1986;	Cialdini	et	al.,	1991;	Cialdini	et	al.,	1990;	WWF,	2012)	and	only	a	few	of	the	FGs’	
participants	challenged	this	normalization;	but	from	the	point	of	view	of	not	being	able	to	afford	it,	rather	
than	not	aspiring	to	such	a	lifestyle.	Findings	from	FGs’	participants	and	ID	interviewees	further	show	that	
as	long	as	it	is	affordable,	they	are	willing	to	pay	more	for	energy	in	order	to	maintain	current	lifestyles.	This	
is	to	say	the	norm	is	rather	towards	the	fulfilment	of	own	needs	and	family	wellbeing,	and	less	toward	
environmental	protection,	(DECC,	2011),	(RQ2).	As	a	result	of	this	reported	normalization,	little	evidence	
could	be	seen	that	would	suggest	that	norms	could	be	used	to	promote	more	energy	efficient	behaviours,	
(RQ3),	though	they	did	appear	to	be	determinants	for	energy	use,	(RQ1b)	and	consequently,	a	change	in	
norms	 could	 reduce	 energy	 use.	 Other	 strong	 determinants	 that	 could	 be	 seen	 related	 to	 building	
characteristics,	as	these	influence,	to	a	greater	degree,	the	amount	and	way	energy	is	used	at	home,	which	
aligns	well	with	the	literature,	(BPIE,	2011;	DGGE/IP-3E,	2004;	Goldblatt,	2005).	Nevertheless,	only	a	few	
FGs’	 participants	 understood,	 or	 have	 been	 aware,	 about	 the	 locked-in	 effect	 that	 this	 situation	
encompasses	 and	 that	 this	 too	 is	 well	 known	 from	 literature,	 (Goldblatt,	 2005;	 Maréchal,	 2010;	 Shove	
2004).		
Energy	prices	were	reported	as	influencing	energy	use,	but	not	that	often	and	provided	further	evidence	in	
support	of	the	literature,	(DECC,	2011;	Gatersleben	et	al.,	2002,	Sorell,	2007),	regarding	energy	use	as	price	
inelastic	in	the	short	term,	but	more	elastic	in	the	long	term.	Nevertheless,	this	reduced	level	of	energy	use	
would,	in	accordance	to	those	relevant	FGs’	participants,	change	if	they	could	afford	to	pay	higher	energy
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bills,	providing	evidence	to	support	literature	that	advocates	higher	incomes	might	lead	to	higher	energy	
use,	(DECC,	2011;	Gatersleben	et	al.,	2002).	Findings	from	the	FGs	and	ID	interviewees	did	thus	show	a	
positive	relation	between	energy	prices	and	energy	use,	as	well	as	between	disposable	income	and	energy	
use.	This	positive	relation	mirrors	earlier	research,	(DECC,	2011;	Gatersleben	et	al.,	2002);	Sorrell,	2007)	and	
has	been,	for	example,	explained	by	the	concept	of	price	elasticity	and	demand	saturation,	(Sorrell,	2007).		
A	further	finding	relates	to	what	is	known	from	the	literature	as	energy	and/or	fuel	poverty,	(Buzar,	2007a;	
Boardman,	2010;	UK	Government,	2013).	During	the	FGs,	a	significant	number	of	participants	from	FG4,	5,	6	
and	7	reported	experiences	that	appear	to	be	situations	of	energy	and/or	fuel	poverty,	which	is	in	line	with	
the	assumptions	from	literature	that	this	would	be	the	case	within	Mediterranean	countries,	(Healy,	2003;	
SEI,	2003;	SILC,	2007;	WHO,	2012).
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7 	Factors	influencing	energy	use	at	home	
Chapter	seven	explores	the	relationships	between	motivations	and	barriers	of	energy	use	in	the	home.	The	
chapter	discusses	the	findings	from	the	energyprofiler	survey	questionnaire	(EP),	the	focus	groups	(FG)	and	
the	in-depth	individual	interviews	(ID)	regarding	what	influences	energy	use	at	home	(RQ2).	
7.1 	Motivational	variables	and	energy	efficient	behaviours	
Motivations	 were	 explored	 initially	 during	 the	 energyprofiler	 (EP)	 survey,	 with	 Q15,	 an	 open-format	
question,	 (Appendix	 VI	 for	 full	 list	 of	 answers)	 and	 then	 further	 explored	 during	 the	 FGs	 and	 ID,	 to,	 in	
particular,	better	understand	the	influence	that	environmental	concerns	could	have	in	terms	of	adopting	
more	energy	efficient	behaviours.	
7.1.1 	The	motivation	for	saving	money	
Findings	from	the	EP	survey	show	that	7	out	of	8	respondents,	(n	=	1.014),	reported	cost-savings	as	the	
most	important	motivation	to	saving	energy.	During	the	FGs	and	CIDs,	to	save	money	was	put	forward	as	
the	 main	 reason	 for	 saving	 energy,	 thus	 reassuring	 the	 earlier	 EP	 findings.	 Moreover,	 the	 motivation	 to	
save,	 for	 monetary	 reasons,	 seemed	 to	 be	 even	 more	 important	 to	 those	 FGs’	 participants	 with	 an,	
apparent,	lower	level	of	disposable	income.	For	this	group	of	less	affluent	FGs’	participants,	energy	costs	
seemed	to	have	a	higher	impact	on	their	disposable	income,	with	participants	reporting	that	it	would	be	
unfeasible	to	accommodate	additional	costs.	Equally	for	FG1,	the	group	that	consisted	of	participants	that	
work	within	the	energy	area	and	that	are	well	aware	of	the	environmental	impact	of	energy	use,	monetary	
motivations	to	save	energy	were	reported	to	be	the	most	important	ones.		
While	cost-savings	had	been	reported	as	the	most	important	motivation,	it	could	be	equally	observed	that	
monetary	motivation	appeared	to	be	in	direct	conflict	with	curtailment	behaviours	that	would	be	required	
to	actually	realize	such	monetary	gains.	FGs’	participants	and	ID	interviewees	frequently	pointed	out	the	
effort	that	would	be	required	to	engage	in	numerous	energy	saving	actions	that,	in	accordance	to	their	
view,	only	result	in	minor	monetary	savings	for	each	of	the	actions	undertaken.	Engagement	in	a	number	of
7.	Factors	influencing	energy	use	at	home	
	
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actions	on	a	daily	basis	and	the	requirement	to	reinforce	the	need	of	such	actions	to	all	family	members	
was	seen	as	inconvenient	and	demanding,	as	illustrated	within	the	following	quotes.	
“I	try	to	do	so,	(switch	lights	off),	but	it's	not	easy.	Sometimes	I	simply	forget	it.	It's	normal”,	
Male	FG6	
“I	sometimes	announce	at	home:	one	of	these	days	I	will	burn	a	CD	to	play	over	and	over,	
telling	things	as	switch	the	lights	off…	switch	this	off…(talking	about	the	need	to	recall	family	
members	what	they	should	do)”,	Female	FG6	
“I	usually	go	around	and	switch	lights	off	and	indeed	I	get	psychologically	more	tired	of	doing	
so	than	the	energy	I	will	save	at	the	end	of	the	month”,	Male	FG3	
As	can	be	seen	from	the	quotes	to	engage	in	repetitive	actions	requires	a	constant	effort,	and	thus	while	
cost-savings	 might	 be	 the	 most	 important	 motivation	 to	 save	 energy,	 in	 practice	 this	 might	 not	 lead	 to	
actual	savings.	
During	the	FGs	and	CIDs,	it	could	also	be	observed	that	a	focus	on	monetary	motivation	might	even	result	in	
an	increased	energy	use,	for	example	by	leaving	low	energy	lights	on,	which	in	literature	is	referred	to	as	
the	rebound	effect,	(Khazzoom,	1980,	Sorrell,	2007,	Gottron,	2001).	Evidence	from	the	FGs	and	CIDs	suggest	
the	existence	of	both,	a	direct	and	an	indirect	rebound	effect.	A	direct	rebound	effect	appeared	to	exists	as	
some	 of	 the	 FGs’	 participants	 reported	 using	 more	 of	 the	 resource,	 instead	 of	 realizing	 the	 energy	 cost	
savings,	for	example,	by	leaving	energy	efficient	light	bulbs	on	since	they	consumed	less,	or	having	longer	
showers,	as	they	were	able	to	buy	bottled	gas	at	a	lower	price.	An	indirect	rebound	effect	appeared	to	exist,	
as	some	FGs’	participants	reported	that	they	would	spend	the	money	saved	on	things	they	could	not	have	
purchased	otherwise.	This	is	to	say	that	a	focus	on	financial	saving	appeared	to	indeed	support	potentially	
energy	and	carbon	intensive	behaviours,	that	then	could	reduce	or,	even	cancel,	the	environmental	benefit	
achieved	through	the	energy	saved.		
In	addition	to	this,	the	focus	on	financial	savings	seemed	to	facilitate	two	misconceptions,	namely	that	the	
use	of	off	peak	tariffs	and	wood	are	ways	to	save	energy.	These	are	misconceptions,	since	in	both	of	such
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cases	energy	is	not	being	saved;	with	off	peak	tariffs	people	consume	the	same	amount	of	energy,	only	pay	
less	for	it	and	by	using	wood	instead	of	gas	or	electricity,	people	might	not	be	saving,	but	rather	substituting	
their	energy	source.		
“One	thinks	there	is	an	associated	cost	and	that	one	needs	to	save.	This	is	the	reason	why	I	
think	about	off	peak	tariffs	and	try	to	use	them	as	much	as	possible”	Female,	FG2	
For	 these	 two	 cases,	 the	 focus	 on	 cost-savings	 could	 have	 easily	 lead	 to	 a	 re-bound	 effect,	 as	 already	
discussed	in	2.3.6	and	6.3.		
7.1.2 	Pro-environmental	behaviour	and	pro-social	motivations	
Pro-environmental	 and	 pro-social	 motivational	 variables	 that	 have	 been	 identified,	 mainly	 related	 to	
environmental	concerns	as	well	as	the	need	for	caring	for	future	generations.	Pro-environmental	and	pro-
social	motivational	variables	that	could	be	observed	related	for	example	to	social	norms,	or	to	personal,	
altruistic	and	moral	motivations,	such	as	environmental	protection,	or	an	individual	feeling	of	doing	the	
right	thing.		
	
During	 the	 EP	 survey,	 the	 environmental	 motivational	 variable	 emerged	 as	 the	 second	 most	 important	
motivation	 to	 save	 energy	 after	 the	 monetary	 stimulus.	 More	 than	 half	 of	 the	 EP	 survey	 respondents	
reported	environmental	motivations	as	a	reason	for	saving	energy,	with	1	in	3	reporting	to	focus	on	saving	
resources	and	1	in	6	reporting	a	concerned	with	climate	change.	During	the	FGs,	the	majority	of	the	FGs’	
participants	reported	similar	motivations	towards	the	environment,	though	monetary	motivation	remained	
predominant,	with	the	environmental	component	perceived	as	a	secondary,	side	effect:		
“It's	an	additional	saving	to	save	on	those,	(environmental),	resources”,	Female	FG6	
Furthermore	1	in	6	respondents	reported	that	they	save	energy	for	the	benefit	of	future	generations,	a	
motivation	that	could	also	be	observed	throughout	the	FGs:
7.	Factors	influencing	energy	use	at	home	
	
138	
“There	 is	 the	 environmental	 motivation	 since	 our	 children	 are	 the	 ones	 bearing	 the	
consequences	of	our	current	habits.”	Female,	FG7	
For	both	the	EP	survey	and	FGs,	the	concern	for	future	generations	seemed	to	be,	however,	comparatively	
low	as	an	individual	priority	and	notably	so,	when	compared	to	the	monetary	variable.	In	4	out	of	the	7	FGs,	
protecting	the	environment	was	put	forward	as	being	the	right	thing	to	do,	the	topic	mainly	came	up	in	the	
context	of	recycling	as	part	of	pro-environmental	behaviour	when	discussing	effective	ways	to	protect	the	
environment.	With	this,	FGs,	and	later	CIDs,	provided	some	evidence	that	saving	energy	could	be	seen	as	
the	right	thing	to	do	for	environmental	reasons,	though	the	following	presented	evidence	suggests	that	this	
actually	might	not	be	the	case.		
The	findings	indicate	that	EP	survey	respondents	and	FGs’	participants	hold	very	positive	attitudes	towards	
the	environment,	not	only	on	a	broader	level,	but	also	towards	energy	and	resource	saving.	During	the	EP	
study	eight	composite	scales	were	computed	resulting	from	the	aggregation	of	questionnaire	items.	Scales	
were	 psychometrically	 validated	 based	 on	 Cronbach	 Alfa/inter-item	 reliability	 analysis	 and	 Pearson’s	
correlation	(for	two	item	scales),	which	can	be	seen	in	the	Table	7-1	below.	
Table	7-1	–	Composite	scales	[n=1.014,	F	(2.89	,	2914.70)	=	434.73,	p	=	.000,	η
2	
=.57],	(Energyprofiler,	2011)..	
Scale/Variable	 Items	(see	questionnaire	in	Appendix	I)	 Reliability	
General	attitude	towards	the	environment	 Q1	(items	1-10,	12,	14,	17)	 α=.82	
Knowledge	on	climate	change	and	energy	 Q1	(items	3,	12,	13,	15,	16)	 α=.65	
Perceived	risk	respond	to	climate	change	 Q1	(items	2	e	4)	 α=.65	
Frequency	of	environmental	performance	 Q7	(items	1-7	+	10-12)	 α=.64	
Attitude	towards	the	conservation	of	energy	and	
natural	resources	
Q1	(items	1,	5,	6,	7,	9,	10,	14	e	17)	 α=.77	
Knowledge	 in	 relation	 to	 energy	 conservation	
measures	
Q1	(items	13	e15)	 α=.70	
Responsibility	in	energy	use	 Q1	(items	11	e	18)	 α=.76	
Attitude	towards	energy	 Q1	(items	1,	6,	9,	10,	14,	17)	 α=.72	
Competence	in	the	use	of	energy	 Q9-14	 α=.52
7.	Factors	influencing	energy	use	at	home	
	
139	
In	 general,	 the	 scales	 had	 acceptable	 (α	 =.	 60)	 to	 high	 (α	 =.	 80)	 internal	 consistency	 levels	 and strong
correlations (r above .50) suggesting	 the	 items	 have	 relatively	 high	 internal	 consistency	 and	 can	 be	
understood	as	a	reliable	measure	of	the	variables	they	represent.	Only	the	competency	measure	in	relation	
to	energy	use	has	low	levels	of	consistency.	One	reason	for	such	could	be	the	fact	the	individual	items	(Q9	
to	Q14)	evaluate	different	aspects	of	energy	consumption	(heating,	use	of	refrigerator,	washing	machine	
and	TV	lighting)	and	as	such	they	might	not	be	perceived	as	part	of	a	single	category.	
Figure	 7-1,	 plots	 the	 average	 Likert	 scale	 values	 for	 the	 composite	 scales	 of,	 “General	 Environmental	
Attitude”,	 “General	 Environmental	 Knowledge”,	 “Risk	 Perceived	 of	 Climate	 Change”	 and	 “Environmental	
Behaviour”,	contained	within	the	EP	survey.	More	information	on	the	EP	study	and	method	are	available	in	
Appendix	VII.	
	
Scale	
General	
Environmental	
Attitude	
General	
Environmental	
Knowledge	
Risk	Perceived	–	
Climate	Change	
Environmental	
Behaviour	
Mean	 4.22	 3.76	 4.29	 3.44	
S.D.	 0.45	 0.57	 0.53	 0.66	
	
Figure	7-1:	Average	values	for	risk	perception	of	climate	change	and	attitude,	knowledge	and	environmental	
behaviour	[n=1.014,	F	(2.89	,	2914.70)	=	434.73,	p	=	.000,	η
2	
=.57],	(Energyprofiler,	2011).	
As	can	be	seen	from	Figure	7-1,	EP	respondents	have	a	high	positive	assessment	of	the	environment	in	
general,	 suggesting	 a	 favourable	 opinion	 regarding	 environmental	 issues	 and	 their	 resolution.	 EP	
respondents	 show	 a	 high	 positive	 attitude,	 towards	 the	 conservation	 of	 natural	 resources	 and	 energy,	
which	 implies	 a	 favourable	 opinion	 in	 relation	 to	 energy	 conservation	 measures	 at	 home.	 Similarly,	 EP	
respondents	reported	having	a	strong	responsibility	towards	energy	use	at	home,	revealing	a	high	level	of
7.	Factors	influencing	energy	use	at	home	
	
140	
importance	in	this	action.	From	another	perspective,	and	as	shown	in	Figure	7-2,	EP	respondents	reported	
and	overall	held,	positive	attitudes	and	knowledge	for	conserving	energy	at	home.		
	
Scale	
Attitude	(…)	
resources	and	
energy	
Attitude	towards	
energy	conservation	
Knowledge	
regarding	energy	
conservation	
Responsibility	towards	
energy	use	
Mean	 4.24	 4.23	 3.64	 4.23	
S.D.	 0.50	 0.53	 0.77	 0.53	
	
Figure	7-2:	Values	for	attitude,	knowledge	and	responsibility	towards	energy	use	[n=1.014;	F	(2.89	,	2914.70)	=	
434.73,	p	=	.000,	η
2	
=.57],	(Energyprofiler,	2011).	
The	 positive	 attitudes	 and	 apparent	 knowledge,	 as	 presented	 in	 Figures	 7-1	 and	 7-2,	 did	 not	 seem	 to	
translate,	however,	into	performance	and	frequency	of	pro-environmental	behaviours.	As	can	be	seen	from	
the	 same	 EP	 survey	 responses,	 (Q7),	 to	 separate	 waste,	 reuse	 bags,	 or	 control	 room	 temperature	 was	
reported	 as	 ranging	 from	 between,	 "Sometimes",	 to,	 "Often",	 depending	 on	 the	 specific	 behaviour,	 as	
Figure	7-3	illustrates.
7.	Factors	influencing	energy	use	at	home	
	
141	
	
Figure	7-3:	Reported	pro-environmental	behaviours	[n=1.014],	(Energyprofiler,	2011).	
The	frequency	of	reported	behaviours,	shown	in	Figure	7-3,	was	thus	significantly	inferior	to	the	positive	
attitude	 shown	 in	 Figures	 7-1	 and	 7-2,	 highlighting	 the	 potential	 inconsistency	 between	 global	
environmental	attitudes	and	pro-environmental	behaviours.	This	is	to	say	that	the	favourable	opinion	of	
environmental	protection	presented	in	Figure	7-1,	apparently	did	not	translate	into	a	high	frequency	of	pro-
environmental	behaviours,	indicating	the	existence	of	an	attitude-behaviour	gap.	This	does	support	earlier	
findings	indicating	that	attitudes	seem	to	have	little	predictive	value	for	explaining	behaviour,	(Geller,	1981;	
McKenzie-Mohr	 &	 Smith,	 1999)	 and	 thus,	 can	 lead	 to	 an	attitude-behaviour	 gap,	(Kollmuss	 &	 Agyeman,	
2002).	
EP	findings	further	show	that	some	pro-environmental	behaviours,	such	as	re-using	bags,	or	turning	off	the	
light	when	leaving	a	room,	are	more	often	reported	than	others,	such	as	using	rechargeable	batteries,	or	
turning	off	the	standby	mode	of	home	appliances.	During	the	FGs	and	the	CID	interviews	the	realtionship	
between	 positive	 environmental	 attitudes	 and	 actual	 behaviours,	 was	 further	 investigated	 to	 better	
understand	the	reasoning.	Findings	indicate	that	the	positive	attitudes	towards	energy	saving	seemed	to	be	
surpassed	 by	 the,	 individual,	 direct	 benefits	 of	 energy	 use,	 such	 as	 comfort	 and	 wellbeing,	 which	 were	
reported	to	rank	higher	on	individual	priorities	as	long	as	they	remain	affordable,	(see	3.4.4.).	This	is	to	say	
that	overall	attitudes	towards	environmental	and	energy	conservation,	as	demonstrated	in	Figures	7-1	and
7.	Factors	influencing	energy	use	at	home	
	
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7-2,	 might	 be	 high	 when	 evaluated	 in	 isolation,	 but	 when	 compared	 to	 other	 factors,	 they	 might	 be	
surpassed.	In	such	cases	there	appeared	a	preference	for	comfort	and	wellbeing,	over	environmental	and	
energy	 conservation.	 Thus	 in	 isolation,	 environmental	 and	 energy	 conservation	 might	 be	 strong	
motivational	variables,	but	in	conjunction	with	other	variables,	they	might	be	comparatively	weak.	In	such	a	
situation,	 saving	 energy	 to	 save	 money	 or	 the	 environment	 enters	 into	 direct	 competition	 with	 the	
expectation	 and	 desire	 of	 maintaining	 established	 practices	 and	 fulfilment.	 This	 is	 well-known	 from	 the	
literature	 with	 suggested	 benefits	 and	 motivations,	 for	 example,	 being	 convenience	 and	 comfort,	
(Barenergy,	2011,	Darnton,	2008,	Darnton	et	al.,	2011,	Jackson,	2005,	Prendergrast	et	al.,	2008).	
A	 further	 observation	 of	 inter-dependent	 and	 inter-related	 factors	 concerns	 financial	 and	 pro-
environmental	 variables,	 in	 conjunction	 with	 differing	 points	 in	 time.	 The	 majority	 of	 FGs’	 participants,	
being	more	or	less	affluent,	demonstrated	concern	with	their	current	financial-economic	situation,	which	
was	seen	as	a	concrete,	near	term	threat,	compared	to	the	potential	consequences	of	their	energy	use	in	
environmental	 terms	 which	 was	 perceived	 as	 a	 more	 abstract	 long-term	 threat.	 This	 was,	 for	 instance,	
expressed	 by	 a	 number	 of	 participants	 through	 their	 understanding	 that	 today’s	 generation	 would	 not	
suffer	the	consequences	of	predicted	environmental	problems.	Only	a	few	FGs’	participants,	and	only	one	
CID	 interviewee,	 reported	 to	 be	 sceptical	 that	 they	 would	 not	 suffer	 at	 all	 from	 such	 negative	
consequences.	 Negative	 consequences,	 referred	 to	 the	 fact	 that	 today’s	 generation	 might	 already	 be	
suffering	 from	 scarcity	 of	 resources,	 such	 as	 petroleum	 or	 water,	 but	 not	 necessarily	 from	 the	
environmental	impacts	of	their	use.	In	the	opposite	direction,	the	financial	economic	crisis	was	described	as	
something	 that	 FG	 participants	 and	 CID	 interviewees	 were	 currently	 experiencing	 and	 perhaps,	 even	
affected	 by	 and	 that,	 therefore,	 did	 concern	 them.	 FGs’	 participants,	 CID	 and	 PID	 interviewees	 also	
acknowledged	 the	 difficulty	 in	 understanding	 the	 relation	 between	 individual	 energy	 use	 and	 the	
environmental	damage,	which	together	negatively	influenced	their	individual	motivation	to	save	energy.	
Some	FGs’	participants	claimed	to	not	be	able	to	understand	the	value	of	the	contribution	of	their	individual	
energy	consuming	behaviours	and	thus	they	do	not	know	whether	their	consumption	could	be	classed	as	
normal	or	not,	as	the	following	quote	shows:
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“What	is	a	normal	use?	How	much	energy	is	it	per	day?	And	if	I	consume	above	that	level,	what	
happens?	Do	I	need	to	use	x	more	kilos	of	coal?	Is	that	what	it	means?	One	cannot	understand”,	
Female,	FG2	
With	this,	it	appeared	as	if	the	inability	of	understanding	the	consequences	of	ones	actions	led	to	a	sense	of	
helplessness	 and	 disempowerment.	 This	 supports	 earlier	 findings	 from	 Thøgersen	 (2005),	 that	 reduced	
levels	of	knowledge,	regarding	the	environmental	impact	of	ones	behaviour,	including	energy	use,	appears	
to	influence	the	ability	to	act	in	accordance	to	individual	positive	environmental	attitudes.	Further	to	this,	
the	majority	of	the	FGs’	participants	perceived	the	behaviours	of	others	as	having	a	more	direct	impact	on	
the	 environment	 then	 their	 own	 energy	 saving	 behaviours.	 There	 was	 a	 strong	 consensus	 among	 FGs’	
participants	that	they	perceived	saving	energy	as	having	a	lower	impact	on	the	environment	in	comparison	
to	other	behaviours,	such	as	water	saving	or	recycling,	though	no	underlying	reasons	could	be	perceived:	
“I	don't	think	one	thinks	I	will	save	energy	in	order	to	protect	the	environment,	I	will	recycle	to	
save	the	environment,	that	might	work	out”,	Male	FG7.	
Another	motivational	variable	that	had	been	examined	was	the	limitedness	of	resources	as	a	motivation	to	
use	less	energy,	which	the	majority	of	the	FGs’	participants	did	not	seem	to	take	into	account.	All	three	CID	
interviewees,	in	contrary,	reported	to	understand	energy	sources	as	something	limited	and	one	reported	
energy	scarcity	as	a	fundamental	reason	to	reduce	his	energy	use.	
In	summary,	the	findings	presented	in	this	section	indicate	that	environmental	motivations	appear	to	not	
play	 an	 important	 role	 in	 inspiring	 people	 to	 adopt	 more	 energy	 efficient	 behaviours	 for	 a	 number	 of	
reasons	 as	 has	 been	 discussed	 through	 this	 section,	 most	 notably	 because	 of	 an	 apparent	 lack	 of	
motivation.	FGs’	responses	have	further	shown	the	potential	existence	of	an	attitude-behaviour	gap,	thus	
support	 earlier	 findings	 provided	 by	 Kollmuss	 &	 Agyeman	 (2002).	 Such	 an	 attitude-behaviour	 gap	 might	
explain	the,	apparent,	observed	dissonance	between	very	positive	attitudes	towards	the	environment	and	
resulting	actions.	Once	it	comes	to	action,	participants	seemed	to	position	environmental	concerns	at	a	
lower	priority	level,	compared	to,	for	example,	financial,	or	family	comfort	and	wellbeing	issues.
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7.1.3 	Needs	and	expectations	and	its	relation	to	motivation	for	saving	energy	
As	can	be	seen	in	section	6.2.5,	social	norms	have	been	found	to	be	potentially	strong	determinants	of	
energy	 use.	 From	 a	 motivational	 perspective,	 social	 norms,	 however,	 did	 not	 appear	 to	 be	 a	 strong	
determinant	to	save	energy	at	home,	though	it	was	extensively	recognised,	once	talking	about	barriers,	as	
detailed	in	section	7.2.	During	the	EP	survey,	only	3.6	percent	were	concerned	with	the	social	component	
for	saving	energy,	or	status,	(2.6	percent),	or	self-image,	(2.7	percent).	Social	norms	were	however	reported	
during	the	FGs,	the	CID	and	PID	interviews,	to	play	an	important	role	in	pro-environmental	behaviours,	such	
as	recycling	and	water	conservation.	As	a	motivational	variable	to	save	energy,	social	norms	were	however,	
reported	to	be	overall	of	low	importance.	This	is	not	surprising,	as	FGs,	the	CID	and	PID	interviews	equally	
did	show	that	current	usage	levels	are	frequently	understood	as	being	normal,	(see	6.2.5),	and	therefore,	
the	social	norm	is	determined	by	current	energy	use,	which	is	expected	to	accommodate	all	needs	and	
expectations.		
7.2 	Barriers	for	adopting	more	energy	efficient	behaviours	
Barriers	 were	 explored	 initially	 with	 Q16	 of	 the	 energyprofiler	 survey,	 in	 an	 open-format	 question,	
(Appendix	VIII	for	full	list	of	answers),	that	asked	respondents	to	provide	their	reason(s)	for	not	trying	to	
save	energy	more	often	at	home.	Findings	indicate	that	EP	respondents	in	the	majority,	believed	they	were	
already	 doing	 everything	 they	 could	 to	 save	 energy	 and	 a	 question	 for	 the	 FGs	 and	 the	 ID	 interviews,	
therefore,	was	to	explore	if	this,	indeed,	has	been	the	case,	or	whether	there	might	be	any	barriers	that	
lead	to	the	conclusion	of	having	done	everything.	The	frequency	of	responses	during	the	FGs	(see	Appendix	
IX	for	full	responses),	when	asked	to	provide	three	reasons	for	not	saving	energy,	are	presented	in	Figure	7-
4,	in	the	form	of	a	word	cloud,	subsequently	shown	in	grouped	format	in	Figure	7-5.
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Figure	7-4:	Reasons	for	not	saving	energy	at	home	–	responses	from	FGs	
	
Figure	7-5:	Frequency	of	category	groups	of	barriers	during	FGs.	
As	will	be	seen	through	this	section,	not	all	such	initial	reasons	for	not	saving	energy	at	home	appeared	to	
ultimately	play	a	role,	while	others	did.	
7.2.1 	External/macro	barriers:	policy	based,	structural	and	economic	barriers	
As	shown	in	Figure	7-5,	economic	conditions	where	put	forward	as	potential	barriers	for	adopting	more	
energy	efficient	behaviours.	FGs’	participants	and	ID	interviewees	put	forward	two	economic	barriers	that,	
both	 could	 be	 classified	 as	 policy	 based	 barriers.	 Firstly,	 a	 few	 FGs’	 participants	 felt	 that	 only	 those	
appliances	that	are	considered	by	law	as	being	energy	efficient	should	be	available	for	purchase.	In	their	
view,	such	compliance	to	minimum	standards	could,	however,	only	be	achieved	through	policy	measures,	
as	postulated	in	the	literature,	(Barenergy,	2011).	Thus	a	lack	of	such	measures	could	be	seen	as	a	barrier.	
Barrier Comfort Habits
Willingness	
Laziness		
Resistance	to	
change
Self-
indulgence
Environment		
Future
Initial	
investment	
Return	on	
the	
investment
Information
Actions	
currently	
taken
Economic	
conditions
Social	
norm,	
social	
dilemma,	
hypocrisy
Frequency 6 4 6 7 6 8 34 9 16 15
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The	second	barrier	discussed	within	five	of	the	FGs,	related	to	penalty	and	incentive	mechanisms	that	could	
promote	 the	 adoption	 of	 more	 energy	 efficient	 behaviour	 at	 home.	 According	 to	 the	 FGs’	 participants,	
penalty	and	incentive	mechanisms	could	only	be	promoted	through	policy-making	interventions	and	thus,	
the	lack	thereof	again	constituted	a	barrier	to	them.	
Two	 more,	 further,	 barriers	 could	 be	 observed	 during	 the	 FGs	 and	 the	 ID	 interviews,	 both	 of	 which	
appeared	 to	 belong	 to	 physical-structural	 barriers,	 namely	 housing	 and	 existing	 home	 appliances.	 The	
infrastructure	 of	 the	 house	 was	 seen	 as	 being	 a	 determinant	 of	 energy	 use	 at	 home.	 This	 barrier	 was	
particular	discussed	in	CID	and	PID	interviews	and	there	was	strong	consensus	regarding	the	importance	of	
house	infrastructure,	as	well	as	the	difficulty	of	intervention,	even	when	technical	and	economic	options	are	
available:	
“There	are	a	set	of	solutions	that	can	protect	the	environment,	namely	in	terms	of	the	way	the	
house	is	build,	that	for	the	reason	of	being	so	expensive	are	not	used”,	Male	FG3	
“I	 have	 the	 limitation	 of	 living	 in	 an	 apartment	 building	 which	 does	 not	 allow	 me	 to	 take	
actions	in	an	independent	way	in	order	to	save	energy”,	CID2	
“If	we	want	to	install	a	solar	panel	they	are	so	expensive”,	Female	FG6	
There	was	a	strong	consensus	that	changing	existing	infrastructure	will	not	only	be	cost	intensive,	but	also	
only	feasible	once	existing	home	appliances	are	out	of	service,	or	when	technological	solutions	become	
more	economically	viable.	As	such,	the	findings	aligned	well	with	the	literature,	(Gardner	and	Stern,	2008;	
Martiskainen,	2007,	Goldblatt,	2005,	Maréchal,	2010).	For	the	case	of	efficiency	behaviours,	with	which	an	
initial	investment	is	required,	not	being	able	to	afford	the	purchase	of	more	energy	efficient	appliances	was	
often	reported	by	FGs’	participants	as	an	economic	barrier	towards	the	adoption	of	more	energy	efficient	
behaviour.	This	barrier	was	more	predominant	within	FGs	4,	5,	6	and	7,	which	appeared	to	be	less	affluent,	
though	it	was	also	discussed	with	a	slightly	different	focus	with	the	remaining	FGs.	In	the	case	of	the	less	
affluent	FGs,	the	discussion	focused	more	on	the	purchase	of	energy	efficient	home	appliances,	the	more	
affluent	concentrated	on	the	need	for	improving	the	building	itself,	or	install	renewable	energy	solutions.	
This	 division	 resembles	 the	 discussion	 from	 section	 2.4.4,	 2.4.5	 and	 6.2.4,	 regarding	 the	 influence	 of
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economics,	 energy	 prices	 and	 income	 levels	 in	 terms	 of	 energy	 use	 at	 home.	 With	 this	 all	 the	 FGs	
considered	economic	aspects	and	financial	limitations	as	constituting	barriers.	For	the	former	group,	the	
barrier	 related	 to	 curtailment	 behaviours,	 while	 for	 the	 latter	 group,	 it	 related	 to	 efficiency	 behaviour,	
similar	to	the	discussion	in	section	6.2.		
7.2.2 	Knowledge	based	barriers	
With	regards	to	knowledge	based	barriers,	the	findings	have	been	somehow	contradictory,	as	the	results	
indicated	 that	 participants	 had	 adequate	 information,	 yet	 they	 argued	 the	 existence	 of	 some	 types	 of	
knowledge	barrier	and	thus,	lack	of	information.	That	participants	had	adequate	information	could	be	seen,	
for	 example,	 from	 EP	 respondents	 who	 reported	 an	 average-high	 level	 of	 general	 environmental	
knowledge,	as	well	as	knowledge	of	measures	for	conserving	energy	at	home.	Furthermore,	half	of	the	EP	
respondents	 reported	 already	 doing	 everything	 they	 can	 and	 1	 in	 5	 reported	 their	 current	 actions	 as	
sufficient.	A	smaller	percentage,	(16.9	percent),	of	the	EP	respondents	reported	that	they	would	like	to	do	
more,	but	did	not	know	how.	Similarly,	lack	of	information	has	been	the	most	often	reported	barrier	for	not	
saving	more	energy	at	home	during	FGs,	as	can	be	seen	in	Figure	7.5	(page	127)	Equally	similar	to	the	EP	
responses,	 the	 wider	 findings	 of	 the	 FGs	 did	 indicate	 that	 participants	 actually	 appeared	 to	 have	 such	
knowledge.	These,	partly	contradictory,	findings	are	presented	below.		
Both,	FGs’	participants	and	ID	interviewees,	frequently	expressed	difficulty	with	regards	to	one	of	three	
aspects:	(1),	lack	of	information	regarding	their	overall	energy	use,	(2),	lack	of	information	regarding	the	
contribution	of	specific	home	appliances	and	behaviours	to	the	total	amount	of	energy	used	and	(3),	as	a	
result	of	the	previous	two	reasons,	a	lack	of	information	regarding	the	amount	of	energy	that	can	be	saved	
by	adopting	more	energy	efficient	behaviours.	
Regarding	 the	 lack	 of	 knowledge,	 in	 terms	 of	 overall	 energy	 use,	 during	 the	 FGs,	 there	 was	 overall	
agreement	towards	the	difficulty	of	understanding	how	much	energy	they	used	at	home.	This	was	even	the	
case	for	participants	of	FG1	that	work	in	the	energy	industry.	This	difficulty	was	perhaps	less	a	result	of	not	
being	 able	 to	 understand	 ones	 energy	 use,	 but	 rather	 due	 to	 the	 lack	 of	 feedback	 systems	 that	 could	
provide	meaningful	real	time	information.
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Men1:	I	have	the	understanding	of	saving	when	I	switch	the	lights	off	that	I’m	saving	
something	but	I	don’t	know	how	much	that	is.	
Men2:	But	that’s	it...you	have	the	feeling...I	substitute	my	TV	against	a	more	energy	efficient	
one	and	I	have	no	idea	how	much	that	could	save	me.	I	can’t	know	since	I	don’t	have	an	
energy	meter...if	I	would	have	one	I	would	now	how	much	I	save,	FG1	
Similarly	 EP	 responses	 on	 providing	 a	 monthly,	 or	 an	 annual,	 figure	 for	 respondents’	 electricity	 and	 gas	
consumption,	 (Q29,	 Q30),	 showed	 a	 significant	 lack	 of	 knowledge	 on	 how	 much	 energy	 is	 used	 on	 a	
monthly	and	yearly	base.	Most	EP	respondents	provided	an	average	annual	cost	for	electricity,	of	126.93€,	
(SD=	133.81€)	and	of	gas,	111.07€,	(SD	=	86.31€).	For	monthly	values,	electricity	corresponds	to	67.55€,	(SD	
=	35.33€)	and	gas	56.27€,	(SD	=	35.94€).	During	the	FGs,	few	participants	reported	how	much	they	pay	for	
energy	and	even	CID	interviewees,	once	asked	directly,	hesitated	in	providing	a	value.	Once	provided,	the	
value	appeared	to	be	rather	an	estimated	value.	In	addition	to	this,	participants	in	four	of	the	FGs	and	also	
CID	interviewees	reported	their	energy	use,	not	in	kW,	but	in	Euros,	thus	indicating	that	the	amount	of	
energy	used	is	not	really	known	and	focuses,	very	much,	on	the	price.	Nevertheless,	this	evaluation	seemed	
to	be	strongly	associated	with	monthly	energy	bills,	(electricity	and	piped	gas	in	Portugal),	and	less	with	
other	energy	sources,	such	as	bottled	gas	or	firewood.	As	an	apparent	consequence,	people	neither	knew	
how	much	energy	they	were	using,	nor	did	they	seem	to	be	able	to	refer	to	energy	in	any	other	variable	
than	the	monetary	one.	
“There	is	no	other	way	to	measure	energy	use,	one	does	not	know,	I	personally	don't	know	
another	way	to	measure	apart	from	the	amount	I	pay	for	energy”	Female,	FG4	
Further,	findings	did	show	an	apparent	disadvantage	to	the	current	design	of	energy	bills,	which	made	it	
difficult	to	separate	an	increase	in	energy	use	from	changes	in	the	price,	or	of	isolating	its	price	from	other	
surcharges	that	are	included	within	energy	bills	in	Portugal.				
In	regard	to	this,	most	of	the	FGs’	participants	did	not	understand	how	to	interpret	the	amount	of	energy	
used;	with	regards	to	if	it	could	be	considered	normal:
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“The	single	indication	I	have	that	I	use	little	energy	is	due	to	the	amount	I	pay	since	I	don't	
even	know	whether	it's	little	or	too	much”	Female,	FG2	
The	majority	of	the	FGs’	participants	claimed	to	not	understand	what	a	normal	energy	use	level	at	home	
would	be.	For	most	of	the	FGs,	a	detailed	discussion	on	what	normal	means,	usually	took	place	at	this	point	
in	terms	of	how	to	define	normal,	what	should	be	included,	or	excluded,	or	how	to	accommodate	specific	
individual	and	family	circumstances.	The	majority	of	the	FGs’	participants	concluded	that	normal	energy	use	
would	 need	 to	 be	 calculated	 in	 relation	 to	 some	 sort	 of	 variable,	 such	 as	 persons	 per	 household.	 FGs’	
participants	showed	a	common	agreement	that	knowing	this	normal	value	for	the	energy	use	at	home,	
would	 allow	 them	 to	 compare	 their	 own	 energy	 use	 with	 others,	 in	 order	 to	 understand	 whether	 their	
energy	use	was	above,	below	or	normal.	
In	terms	of	the	contribution	of	specific	home	appliances	and	behaviours,	the	majority	of	FGs’	participants	
and	CID	interviewees	revealed	several	doubts	regarding	the	contribution	of	different	home	appliances	and	
energy	related	practices:	
“I	don't	feel	ready	to	reduce	the	energy	I	use.	I	don't	know	how	much	each	appliance	is	using,	
each	lamp	and	as	a	consequence	I	can't	reduce	the	energy	used”	Female,	FG4	
“Last	year	I	bought	an	electrical	oven	(…)	and	I	was	curious	to	see	how	much	energy	it	used	so	
I	would	do	a	roast	or	bake	a	cake	and	would	check	for	how	much	energy	it	was	using.	And	I	
learned	 that	 for	 a	 roast	 I	 needed	 4,	 a	 cake	 2	 (referring	 to	 energy	 units),	 I	 already	 cannot	
remember	but	by	that	time	I	learned	how	much	energy	I	was	using”	Female,	FG7	
“1st	women:	I	think	that	we	don't	know	things	we	could	to	do	(to	save	energy)	2nd	women:	
and	other	times	we	don't	do	because	we	do	not	want	to	pay	attention	to	the	information”	
Female,	FG6	
While	 the	 quotes	 above	 illustrate	 doubts	 regarding	 the	 contribution	 of	 different	 home	 appliances	 and	
energy	related	practices,	they	also	illustrate	an	apparent	unwillingness	to	engage	and	lack	of	interest	in	the	
subject.	 With	 regards	 to	 the	 perceived	 overall	 energy	 saving	 potential	 at	 home,	 only	 a	 quarter	 of	 EP
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respondents	answered	the	question,	(Q31),	regarding	the	potential	for	saving	energy	at	home,	reporting	an	
average	 saving	 of	 16.48	 percent.	 One	 of	 the	 respondents	 reported	 the	 potential	 reduction	 in	 Euros,	
reaching	 an	 average	 of	 18.05	 Euros	 per	 month,	 which	 was	 less	 than	 the	 percentage	 cited.	 This	 again	
suggests	 some	 difficulty	 in	 evaluating	 and	 calculating	 energy	 saving	 potentials.	 This	 difficulty	 of	
understanding	energy	use	and	the	saving	potential	of	specific	behaviours	was	further	demonstrated	once	
EP	respondents	were	asked	to	list	five	energy	saving	behaviours,	from	the	one	that	saves	most	energy	to	
the	one	that	saves	the	least,	(Q8).	The	list	of	the	five	energy	saving	behaviours	included	the	following:	(1),	
“Use	the	washing	machine	and/or	dishwasher	at	low	temperature	(30-40º)”;	(2),	“Defrost	periodically	the	
fridge/freezer”;	 (3),	 “Replace	 incandescent	 light	 bulbs	 by	 fluorescent	 ones”;(4),	 “Turn	 off	 an	 appliance	
instead	of	leave	it	in	stand-by”;	and	(5),	“Reduce	the	shower	time	from	15	to	10	minutes”.	EP	survey	results	
show	 that	 the	 ordering	 is	 not	 aligned	 with	 the	 actual	 impact	 of	 the	 five	 behaviours	 computed	 by	 the	
energyprofiler	project	team.	According	to	the	project	teams’	calculations,	the	individual	behaviour	with	the	
highest	potential	for	saving	energy	would	be	to	reduce	shower	time,	followed	by	eliminating	all	stand-by	
consumptions.	EP	respondents	considered	those	two	options	however	to	be	of	a	lower	impact,	with	only	
17.76	percent	considering	a	reduced	shower	time	and	12.95	percent	considering	eliminating	all	stand-by	
consumptions	as	having	a	high	impact.	Instead,	“Replacing	incandescent	light	bulbs	with	fluorescent	ones”,	
had	the	highest	percentage,	(77.53	percent),	followed	by	”Using	the	washing	machines	in	programs	for	low	
temperatures”,	 (70.65	 percent).	 This	 suggests	 that	 EP	 respondents	 might	 lack	 knowledge	 regarding	 the	
impact	of	specific	energy	saving	behaviours.	However,	this	finding	should	be	evaluated	carefully,	since	not	
being	able	to	order	a	pre-given	number	of	behaviours,	does	not	automatically	imply	that	EP	respondents,	in	
general,	 possess	 limited	 knowledge	 of	 the	 subject	 domain.	 In	 fact,	 what	 it	 suggests	 is	 that	 respondents	
might	 have	 some	 difficulty	 in	 comparing	 behaviours	 and	 understanding	 their	 individual	 contribution	
towards	energy	savings.	Finally,	EP	respondents	were	invited	to	provide	information	on	everything	they	did	
to	 save	 energy,	 (Q6),	 (Appendix	 VI)	 and	 the	 results	 suggest	 a	 good	 level	 of	 knowledge	 regarding	 both,	
efficiency	and	curtailment	behaviours,	which	could	save	energy	at	home.	Equally,	FGs’	participants	were	
asked	for	the	same	type	of	information,	with	the	results	being	presented	in	Figure	7-6,	listing	all	of	these	
behaviours	that	were	discussed	during	the	FGs.
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Figure	7-6:	Energy	efficient	behaviours	discussed	during	the	FGs.
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As	Figure	7-6	shows,	during	the	FGs	a	number	of	energy	efficient	behaviours	have	been	discussed	and	the	
majority	of	the	FGs’	participants	were	able	to	identify	the	best	practices	under	specific	contexts.	However,	
some	respondents	at	the	same	time,	seemed	to	lack	the	level	of	knowledge,	(Q8,	Q31),	that	would	enable	
them	to	compare	different	specific	behaviours,	or	to	evaluate	the	saving	potential	they	could	achieve.	FGs’	
participants	and	CID	and	PID	interviewees	strongly	agreed	that	not	knowing	the	individual	contribution	of	
energy	consuming	behaviours	could	influence	the	adoption	of	more	energy	efficient	behaviour.		
In	summary,	interpreting	the	data	collected,	within	the	EP,	FGs	and	CIDs,	regarding	the	level	of	information	
held	proved	to	be	difficult,	as	well	understanding	how	far	a	lack	of	knowledge,	could	be	considered	as	a	
barrier.	At	first	glance,	there	seems	to	be,	what	is	well	known	from	the	literature,	an	information-behaviour	
gap,	(Jackson,	2005;	Schultz,	2002;	Southerton	et	al.,	2011;	Stern,	1999),	since	people	report	a	high	level	of	
knowledge	on	the	different	subjects	discussed,	but	then	do	not	seem	to	act	in	accordance.	Findings,	have	
however,	also	shown	that	once	looking	at	a	more	specific	aspect,	or	more	detailed	information,	it	appears	
that	knowledge	and	information	are	not	barriers	as	such,	but	rather	a	convenient	excuse	for	not	taking	
action.	Such	findings	are	equally	known	from	the	literature,	with	previous	research	highlighting	that	people	
tend	 to	 verbalize	 an	 inability	 to	 do	 something,	 (Baker	 and	 Kirsch,	 1991),	 as	 a	 way	 to	 deny	 personal	
responsibility	for	dealing	with	a	problem.	In	the	majority	of	cases,	a	general	need	for	being	provided	with	
targeted	and	useful	information,	that	could	support	individual	decision	and	close	information	circles,	could	
be	observed	across	the	different	research	phases.		
7.2.3 	Cultural-normative-social	barriers	
The	evolution	of	cultural	and	social	norms	influence	energy	use	at	home	and	thus,	can	act	as	a	barrier	to	the	
adoption	of	more	energy	efficient	behaviours,	(see	3.3.4).	This	is	to	say	that	adopting	more	energy	efficient	
behaviours,	might,	challenge	existing	ways	of	thinking	and	doing:	the	social	customs	and	ways	of	living	and	
the	 assumptions	 that	 support	 these	 attitudes	 and	 behaviours	 that	 as	 a	 consequence	 represent	 cultural,	
normative	and	social	barriers	to	change.	During	the	FGs,	a	number	of	examples	of	cultural-normative	and	
social	barriers	could	be	identified.	First	of	all,	the	fact	that	social	norms	seems	to	accept	a	level	of	energy	
use	without	being	perceived	as	overuse.	Many	FGs’	participants	defined	their	energy	use	as	being	usual,	
habitual,	or	normal	and	thus	showed	no	actual	need	to	save	energy;	FGs’	participants	seemed	to	be	quite
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comfortable	 with	 how	 society	 will	 judge	 their	 energy	 use.	 An	 exception	 to	 this	 normal	 energy	 use	 was	
discussed	by	a	few	FGs’	participants,	who	reported	the	pressure	from	society	to	reduce	energy	use	and	to	
behave	in	a	way,	outlined	by	the	participants	as	being	green,	in	order	to	fit	the	social	norm.	Those	FGs’	
participants	equally	expressed	that	this	perceived	need	of	being	green,	might	even	result	in	reporting	things	
that	they	do	not	actually	do	in	order	to	fulfil	the	social	expectations:	
“To	fit	the	society	norm	people	say	I	save,	I	do	all	but	in	reality	they	do	nothing”,	Female	FG7	
As	 an	 example	 of	 how	 social	 norms	 can	 influence	 individual	 behaviour,	 FGs’	 participants	 frequently	
highlighted	two	cases:	recycling	and	saving	energy.	They	felt	that	for	recycling,	the	social	norm	expected	
one	 to	 recycle,	 while	 for	 energy	 saving	 this	 was	 not	 the	 case.	 For	 energy,	 the	 majority	 of	 the	 FGs’	
participants	 and	 all	 three	 CID	 interviewees	 reported	 to	 feel	 somehow	 entitled	 to	 overuse	 energy	 and	
admitted	an	egoistic	focus,	i.e.	a	focus	on	fulfilling	individual	needs	the	way	they	wanted.	
Overall	however,	the	question	of	what	could	be	understood	as	normal	use	of	energy	remained	unanswered.	
This	 topic	 was	 thus	 further	 explored	 during	 the	 ID	 with	 both,	 energy	 consumers,	 (CID)	 and	 energy	
intervention	providers,	(PID).	CID	interviewees	were	asked	to	choose	one	of	five	alternatives,	(high,	normal,	
average,	reduced	and	conditioned),	that	could	best	describe	their	energy	use	at	home.	Those	five	categories	
were	chosen	in	order	to	use	the	terminology	that	FGs’	participants	used	during	their	discussion	when	they	
described	 their	 energy	 use	 at	 home.	 Two	 out	 of	 three	 CID	 interviewees	 considered	 their	 energy	 use	 as	
average	and	one	as	normal,	which	mirrored	the	FGs’	results.	During	the	CID	interviews	it	was	possible	to	
underpin,	to	a	certain	degree,	this	understanding	of	normal	and	average.	CID	interviewees	evaluated	their	
energy	use	as	normal,	or	average,	in	comparison	to	what	their	friends	and	family	used,	as	well	as	how	much	
they	paid	for	energy.	Normal	or	average	energy	use	was	additionally	defined	by	all	three	CID	interviewees,	
through	a	self-evaluation	process	by	comparing	what	they	did	to	what	they	know	the	best	practices	were.	
Yet,	normal	energy	use	also	seemed	to	equal	minimum	energy	use.	Once	asked	about	what	could	be	seen	
as	the	possible	minimum	energy	use	at	home,	CID	interviewees	enumerated	a	number	of	situations	that	
were	also	perceived	by	them	as	being	current	normal	energy	usage,	such	as	having	a	reasonable	amount	of	
light,	room	temperature,	or	the	number	of	showers	required	to	feel	clean.
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In	summary,	from	a	consumer’s	point	of	view,	there	seemed	to	be	an	understanding	that	their	energy	use	is	
in	line	with	that	of	their	friends	and	family,	therefore	it	is	seen	as	being	normal.	PID	interviewees	reinforced	
the	perception	that	people	will	base	their	understanding	of	normal	use	on	the	amount	of	energy	used,	on	a	
daily	basis,	to	fulfil	their	needs.	One	of	the	PID	interviewees	highlighted	this	perception	of	normal	use	as	
being	influenced	by	society	and	current	lifestyles.	Two	of	the	PID	interviewees	further	highlighted	the	need	
of	defining	normal	energy	use,	taking	into	consideration	the	different	variables	that	influence	energy	use	at	
home,	whilst,	latterly,	being	able	to	communicate	these	to	the	consumer.	
7.3 	Individual	psychological	factors	as	a	barrier	
Individual	 psychological	 factors	 such	 as	 comfort,	 habits,	 willingness,	 laziness,	 resistance	 to	 change,	 self-
indulgence,	 or	 actions	 that	 individuals	 have	 been	 already	 taken	 at	 one	 point	 in	 time,	 are	 all	 potential	
barriers	towards	to	the	adoption	of	more	energy	efficient	behaviour	and	are	discussed	below.	
7.3.1 	Habits	as	an	obstacle	to	the	adoption	of	more	energy	efficient	behaviours	
Habits	and	practices	are	considered	to	influence	energy	use,	in	both	ways,	i.e.,	if	bad	habits	exist	they	will	
increase	 energy	 use,	 or	 good	 energy	 habits	 will	 decrease	 use,	 (see	 3.4.1.).	 FGs’	 participants	 and	 CID	
interviewees	shared	an	understanding	that	a	great	number	of	behaviours	are	habitual	in	nature	and	impact	
their	daily	life,	as	the	following	quotes	exemplify:	
“Human	beings	are	creatures	of	habits,	regardless	whether	you	like	it	or	not	(…)	people	get	
used.	Human	beings	are	creatures	of	habits,	it's	a	routine”,	Female,	FG2	
“It's	really	an	habit,	I	enter	a	room	and	I	switch	the	light	on,	I	could	go	back	and	switch	the	one	
before	off	but	I	don't	and	I	go	further	on	like	this”,	Female	FG4	
“I	simply	forget	it,	(to	switch	appliances	really	off	avoiding	standby	consumption)”,	 Female	
FG7	
Habits	 and	 practices	 were	 perceived	 as	 being	 acquired	 over	 time	 and	 performed	 in	 an	 automatic	 way,	
highlighting	the	habitual	character	of	energy	related	behaviours:
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“There	are	habits	that	are	easier	to	change	than	others”,	Female,	FG2	
“Those	are	habits,	some	people	like	to	switch	lights	on”,	Male,	FG4	
“I	 didn't	 have	 that	 habit,	 but	 I	 started	 switching	 appliances	 really	 off	 to	 avoid	 standby	
consumption”,	Female,	FG7	
The	majority	of	the	FGs’	participants	agreed	that	adopting	more	energy	efficient	habits	might	be	hard	to	
achieve,	and	even	if	managing	to	do	so,	it	was	felt	that	this	would	lead	to	a	reduced	impact	in	terms	of	the	
energy	that	was	used,	or	saved.	Once	approached	on	this	topic,	some	of	the	FGs’	participants	highlighted	
that	they	were	well	aware	of	some	undesirable	habits	that	would	lead	to	higher	than	necessary	energy	use,	
such	as	showering	practices,	having	the	TV	on	even	if	not	watching	it,	or	not	switching	the	lights	off	once	
leaving	the	room.	Though	being	aware	about	such	undesirable	habits,	almost	all	of	the	participants	still	
found	 it	 hard	 to	 change	 them.	 In	 their	 view	 changing	 habits	 would	 require	 an	 individual	 effort	 of	
remembering	and	repeatedly	performing	the	desirable	practice.	
“We	as	human	beings	develop	habits	which	are	later	on	hard	to	renounce	or	change”,	CID2	
Three	 main	 reasons	 were	 provided,	 during	 the	 FGs	 and	 the	 ID	 interviews,	 for	 the	 difficulty	 of	 changing	
habits.	First	of	all,	most	of	the	FGs’	participants	reported	the	general	difficulty	in	changing	any	type	of	habit	
and	this	is	well	reported	in	literature,	(IPPR,	2009;	Green	Alliance,	2011).	This	was	seen	to	be	particular	true	
when	the	overall	objective	was	to	save	energy	by	engaging	in	numerous	individual	actions	that,	individually,	
only	 result	 in	 minor	 monetary	 savings	 for	 each	 action.	 Secondly,	 FGs’	 participants	 and	 CID	 interviewees	
agreed	that	habits	provided	a	level	of	comfort,	convenience	and	well-being,	that	allowed	them	to	be	lazy	
and	self-indulgent,	repeated	what	they	are	used	to	doing	and	what	seemed	to	work,	again	these	findings	
are	well	in	support	in	literature,	(see	section	 3.4.1.).	This	resistance	was	found	in	almost	all	established	
behaviours	during	the	FGs	and	CIDs.	However,	resistance	was	particularly	predominant	on	changing	the	
number,	 duration	 and	 temperature	 of	 showers,	 heating	 rooms	 during	 winter,	 avoiding	 standby	
consumption	or	switching	lights	off:
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“No,	I	don’t	close	the	water	once	washing	myself.	No,	I	open	the	water,	in	the	meantime	I	get	
undressed	the	water	is	running	to	get	the	right	temperature,	I	get	in	and	the	water	keeps	on	
running”,	Female5,	FG2	
Male2:	If	someone	would	tell	me	that	in	the	summer	I	could	only	have	one	shower…I	would	be	
very	disappointed…	
Male3:	no	for	me	it’s	also	a	question	of	duration…I	take	ages	in	the	shower,	it’s	one	of	those	
things	that	make	me	feel	good.	
Male2:	but	do	you	close	the	water	once	washing	yourself?		
Male4:	no		
Male2:	why?	
Male4:	because	of	convenience,	self-indulgence,	FG3	
Thirdly,	 and	 related	 to	 this	 resistance	 of	 changing	 habits,	 the	 majority	 of	 FGs’	 participants	 and	 CID	
interviewees	 revealed	 scepticism	 regarding	 the	 impact	 of	 changing	 such	 habits	 in	 terms	 of	 the	 saving	
potential	that	could	be	realized	and,	as	will	be	discussed	in	more	detail	in	section	7.2.3.,	on	self-efficacy	and	
expectations	regarding	the	outcome	of	own	behaviour.	
However,	 it	 could	 also	 be	 observed	 that	 a	 constant	 awareness	 of	 some	 of	 the	 FGs’	 participants,	 might	
eventually	lead	to	an	unfreezing	of	old	habits,	as	described	by	Giddens	(1984),	that	would	allow	for	new	
habits	to	form.	
“My	conscience	is	already	saying,	no,	go	back	and	switch	that	light	off”,	Female	FG7	
Nonetheless,	some	of	the	FGs’	participants,	and	of	the	CID	and	PID	interviewees,	agreed	that	if	one	could	
see	the	impact	of	habits	on	the	energy	bill,	then	this	could	facilitate	individual	behavioural	change:	
“If	someone	would	explain	and	prove	to	me	that	changing	an	old	habit	will	have	a	significant	
impact	on	my	energy	bill	and	on	the	environment	I	don't	think	it	would	be	too	complicated	to	
change”,	CID1
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During	the	FGs	and	CID	interviews,	a	group	of	participants	and	interviewees	could	be	identified	that	seemed	
to	think	and	act	in	a	different	way.	This	group	appeared	to	behave	more	often	in	a	more	energy	efficient	
way,	 as	 a	 consequence	 of	 the	 way	 they	 were	 educated	 and	 raised	 from	 an	 early	 age.	 One	 of	 the	 CID	
interviewees	explained	the	difference	between	her	and	her	partner’s	energy	use	and	that	this	was	related	
to	 the	 different	 education	 that	 they	 received	 in	 their	 parents’	 home,	 which	 would	 have	 influenced	 and	
remained	into	adulthood.	All	three	CID	interviewees	argued	that	some	habits,	such	as	leaving	light	on/off,	
was	 something	 they	 got	 used	 to	 doing	 from	 an	 early	 age	 and	 that	 those	 habits	 remained	 over	 time	
becoming	perceived	as	normal.	For	those	already	used	to	saving	energy,	not	saving	was	considered	to	be	
irrational,	a	waste.	This	could	be	a	reason	for	an	overall	agreement,	among	FGs’	participants	and	CID	and	
PID	interviewees,	towards	an	effort	to	educating	younger	generations,	to	enable	them	to	understanding	the	
impact	of	their	behaviours	and	positively	to	help	in	educating	a	more	energy	and	environmental	responsible	
generation.	
The	above	discussion	shows	that	habits	seem	to	play	an	important	role	in	energy	use	at	home	and	are	part	
of	one’s	narrative	once	discussing	the	topic.	Participants	used	habits	to	justify	doing	things	the	way	they	do	
it,	 be	 it	 positive	 or	 negative	 and	 these	 habits	 need	 to	 be	 taken	 into	 consideration	 when	 promoting	 the	
adoption	of	more	energy	efficient	behaviour.		
7.3.2 	Comfort	and	convenience		
Maintaining	current	levels	of	comfort	seem	to	be	fundamental	to	FGs’	participants	and	CID	interviewees.	
Saving	energy	was	often	perceived	as	impacting	current	levels	of	comfort,	or	as	one	of	the	PID	interview	
suggested,	interventions	should	be	rather	targeted	at	promoting	energy	conservation,	thus	avoiding	energy	
wastage,	 instead	 of	 focusing	 on	 saving	 energy,	 as	 this	 is	 often	 associated	 with	 losing	 comfort.	 This	
relationship	between	saving	energy	and	a	reduced	level	of	comfort,	were	predominant	responses	within	
FG1,	FG2	and	FG3,	where	participants	seemed	to	have	more	disposable	income	to	spend	on	energy	and	as	a	
consequence,	were	willing	to	trade-off	comfort	and	wellbeing,	for	more	energy	use	and	less	savings.	This	is	
also	known	from	literature,	as	the	impact	of	saving	energy,	on	disposable	income,	might	be	insufficient	to	
motivate	individual	action	to	save	energy,	since,	for	example	BPIE’s	research	(2011),	suggests	that	for	most	
households,	 energy	 bills	 account	 for	 a	 small,	 (3-4	 percent),	 share	 of	 their	 disposable	 income	 and	 thus
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constitutes	a	barrier	for	meaningful	action	towards	reduced	energy	use.	However,	a	distinction	could	be	
seen	during	the	FGs	and	the	ID	interviews,	between	behaviour	that	could	impact	comfort	and	those	that	
were	just	inconvenient	to	do.	Examples	of	comfort	reduction	included	reducing	shower	duration,	or	room	
temperature,	with	examples	of	inconvenience	being	the	need	to	get	out	of	bed	to	really	switch	the	TV	off,	
instead	of	leaving	it	set	on	standby	mode.	Several	FGs’	participants	felt	strongly	that	convenience	could	be	
linked	 to	 laziness	 and	 self-indulgence,	 in	 the	 sense	 that	 it	 was	 more	 convenient	 to	 leave	 appliances	 on,	
instead	of	really	switching	them	off	and	later,	on	again.	Overall,	there	was	a	tendency	to	consider	family	
wellbeing	 as	 more	 important,	 than	 the	 financial	 or	 the	 environmental	 impact	 for	 saving	 energy.	 In	
particular,	for	those	cases	where	FGs’	participants	were	parents,	their	children	were	reported	as	having	a	
significant	 impact	 on	 the	 energy	 use	 at	 home	 and	 this	 does	 not	 always	 mean	 using	 energy	 in	 an	
unsustainable	 way.	 This	 influence	 starts	 at	 an	 early	 age,	 with	 parents	 reporting	 the	 need	 for	
installing/improving	their	heating	systems,	or	of	increasing	room	temperature,	in	order	to	maintain	family	
wellbeing:	
“At	home	we	only	installed	a	heating	system	once	our	child	was	born”,	Female,	FG7	
However,	having	children	at	home	seems	to	have	a	higher	influence,	once	children	get	older	and	adopt	less	
energy	efficient	behaviours,	such	as	leaving	the	lights,	computer	or	TV	on	as	well	as	having	longer	showers.	
This	 connects	 back	 to	 the	 need	 for	 educating	 this,	 new,	 generation,	 in	 order	 to	 better	 understand	 the	
impact	their	behaviour	can	have	and	promoting	the	development	of	more	energy	efficient	expectations.	
Overall,	comfort	and	convenience	appeared	to	constitute	a	clear	barrier	towards	reducing	energy	use	at	
home,	which	is	also	known	from	literature	as	being	a	strong	reason,	(e.g.	Barenergy,	2011,	Darnton,	2008,	
Darnton	et	al.,	2011,	Jackson,	2005,	Prendergrast	et	al.,	2008).	
7.3.3 	Efficacy	and	outcome	expectations	
The	initial	findings	from	the	EP	survey	questionnaire	suggested,	that	respondents	held	a	low	level	of	self-
efficacy	towards	the	adoption	of	more	energy	efficient	behaviours,	with	more	than	half	of	EP	respondents	
reporting	to	already	be	doing	everything	they	can	in	order	to	save	energy	at	home	and	with	22.1	percent	
reporting	 that	 they,	 “Save	 already	 enough”.	 In	 contrast,	 the	 majority	 of	 FGs’	 participants	 and	 CID
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interviewees,	when	asked	if	they	agreed	with	such	a	statement,	rejected	that	they	could	be	already	doing	
everything	they	can	do	to	save	energy	at	home.	Most	FGs’	participants	strongly	felt,	that	there	is	always	
something	 one	 can	 do	 to	 save	 energy	 at	 home,	 which	 indicates	 a	 level	 of	 self-efficacy	 regarding	 their	
potential	 to	 save	 energy	 at	 home.	 However,	 this	 opinion	 gradually	 changed	 during	 the	 FGs’	 discussion,	
when	 the	 discussion	 moved	 from	 the	 abstract	 level	 of	 saving	 energy,	 to	 specific	 behaviours	 that	 were	
explored	in	more	detail.	When	asked	for	the	reasons	for	not	saving	more	energy	at	home,	a	number	of	the	
FGs’	participants	used	their	existing	energy	saving	behaviours	as	a	reason	for	not	saving	further.	As	such,	
reporting	to	already	act	in	a	more	energy	efficient	way,	apparently,	provided	a	feeling	of	indulgence	that	
justified	no	need	to	take	further	action.	The	findings	from	the	EP,	show	that	16.9	percent	of	respondents	
claim	that	they	would	like	to	do	more,	but	do	not	know	how,	while	only	2.3	percent	do	not	believe	their	
efforts	towards	saving	energy	would	be	worthwhile.	In	contrast	to	the	EP	findings,	the	majority	of	the	FGs’	
participants	and	CID	interviewees	appeared	to	be	confident	regarding	their	ability	to	adopt	more	energy	
efficient	behaviours,	with	emerging	narratives	revealing	that	they	were,	nevertheless,	unsure	regarding	the	
outcome	of	such	behaviour	in	terms	of	energy	used	and	saved.	During	both,	FGs	and	CIDs,	there	were	no	
significant	differences	regarding	the	topic	that	appeared	to	be	noteworthy.	Some	of	the	reasons,	for	such	
disbelief,	 on	 the	 outcomes	 provided	 by	 FGs	 and	 CIDs	 include,	 the	 need	 for	 collective	 action	 and	 that	
individual	responses	alone	would	not	be	sufficient.	As	one	FG	participant	summarized	it:	
“I	 can	 know	 how	 to	 perform	 more	 energy	 efficient	 behaviours,	 but	 if	 the	 remaining	 family	
members	don’t	do	the	same	them	his	effort	might	be	easily	cancelled	off.”	Male,	FG3	
For	all	of	the	FGs,	though	to	a	varying	degree,	the	discussion	seemed	to	move	from	a	question	of	being	
able,	to	being	willing	to	adopt	more	energy	efficient	behaviours,	when	comparing	individual	and	collective	
efforts.	Being	able	and	being	willing,	seemed	to	be	aligned	when	discussing	change	in	the	easy	and	simple,	
rather	than	difficult	and	complicated	behaviour.	In	terms	of	saving	energy,	as	something	easy	and	simple	to	
do,	meaning	just	a	matter	of	changing	habits,	appears	to	be	valid	for	those	day-to-day	actions	that	do	not	
require	much	effort	to	perform	and	that	do	not	impact	on	the	level	of	comfort	and	wellbeing	at	home.	FGs’	
participants	provided	some	examples	of	such	behaviours	that	they	reported	to	be	willing	to	change	namely,	
switching	lights	off,	cooking	with	the	lids	on	and	reducing	the	number	of	times	and	duration	of	opening	the
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fridge.	Avoiding	standby	consumption	was	not	always	reported	as	being	easy,	since	there	is	a	convenience	
factor	attached	to	the	behaviour	that	was	reported	as	hindering	best	practice.	The	perception	of	behaviours	
that	were	difficult	to	change	included	those	that	were	directly	associated	with	perceived	and	desired	levels	
of	 comfort	 and	 wellbeing,	 such	 as	 reducing	 room	 temperature	 or	 reducing	 the	 number	 and	 duration	 of	
showers.	This	question	of	evaluating	how	easy,	or	difficult,	it	would	be	to	save	energy,	was	further	explored	
during	the	ID	interviews	where	interviewees	were	asked	how	easy,	or	difficult,	they	found	energy	saving	at	
home	 to	 be.	 CID	 interviewees	 were	 divided,	 with	 two	 reporting	 it	 to	 be	 difficult	 and	 one	 considering	 it	
moderately	easy.	Once	asked	to	explain	their	choice,	CID	interviewees	provided	a	list	of	reasons	for	energy	
savings	 to	 be	 considered	 difficult	 to	 achieve,	 namely,	 existing	 ingrained	 habits,	 unwillingness	 to	 change	
those	habits,	the	need	to	invest	in	order	to	realize	significant	savings,	the	focus	on	maintaining	comfort	
levels,	as	well	as	the	fact	that	individual	efforts	can	be	negated	by	other	family	members’	non-saving	habits.	
Similar	 answers	 were	 reported	 by	 PID	 interviewees	 that	 considered	 energy	 saving	 as	 something	 easy	 to	
achieve,	or	at	least	to	reduce	the	amount	of	wasted	energy,	but	simultaneously,	also	as	something	difficult	
to	achieve.	PID	interviewees	argued	that	people	do	not	hold	enough	information	in	order	to	understand	
and	realize	their	energy	savings	in	terms	of	their	energy	bills	and	as	a	consequence,	this	could	lead	to	the	
abandonment	 of	 energy	 saving	 behaviours,	 in	 particular	 where	 previous,	 negative	 energy	 saving	
experiences	could	work	as	a	barrier	towards	future	energy	saving	attempts.	With	regards	to	information,	
knowledge	and	self-efficacy,	the	PID	assumptions	were	aligned	with	EP	and	FGs’	responses	that	they	felt	
they	had,	overall,	a	good	understanding	on	how	to	save	energy,	including	the	behaviours	that	might	need	to	
be	changed	to	save	energy.	
In	 summary,	 it	 might	 be	 inferred	 from	 the	 findings	 that	 EP	 respondents,	 FGs’	 participants	 and	 CID	
interviewees,	overall	hold	a	good	level	of	knowledge,	that	could	help	them	adopt	more	energy	efficient	
behaviours	and	as	such,	appear	to	believe	they	have	the	ability	to	adopt	those	behaviours	it	they	want	to,	
but,	that	for	some	reason,	they	resist	and	are	unwilling	to	doing	so,	as	explored	further	in	the	following	
section.
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7.3.4 	Resistance	to	and	unwillingness	to	change	
During	the	FGs	and	CIDs,	an	apparent	resistance	and	willingness	to	change	could	be	observed	amongst	the	
interviewees	 and	 three	 broad	 reasons	 could	 be	 identified	 for	 this.	 Firstly,	 the	 majority	 of	 the	 FGs’	
participants	and	all	three	CID	interviewees	reported	a	disbelief	regarding	the	outcomes	of	their	actions,	
notably	on	the	amount	of	energy	that	could	be	indeed	saved,	by	adopting	more	energy	efficient	behaviours.	
FGs’	participants	and	CID	interviewees	expressed	an	overall	frustration,	regarding	the	outcomes	of	previous	
behaviour	change	attempts	in	order	to	save	energy	at	home.	Not	being	able	to	realize	the	outcome	of	their	
savings,	 was	 reported	 by	 the	 majority	 of	 the	 FGs’	 participants	 and	 by	 all	 three	 CID	 interviewees,	 as	
influencing	 not	 only	 the	 abandonment	 of	 the	 newly	 acquired	 behaviour,	 but	 also	 as	 influencing	 future	
attempts	to	save	energy,	as	they	felt	discouraged	by	such	attempts:	
“I	stopped	doing	so,	(unplugging	appliances	and	switching	lights	off),	since	the	invoice	went	
up	once	I	was	doing	it	(…)…I	got	disappointed	and	currently	I	just	don't	care,	I	do	my	normal	
use””	Male,	FG7	
“My	individual	perception	is	that	by	switching	the	light	off	20	seconds	before	won’t	solve	my	
problem	of	reducing	my	energy	bill”,	CID1	
These	quotes	highlight	the	low	outcome	expectancy	associated	with	curtailment	behaviour.	During	the	FGs,	
it	 was	 possible	 to	 observe	 that	 expectations	 were	 apparently	 different,	 once	 it	 came	 to	 efficiency	
behaviours	that	required	an	investment	in	more	energy	efficient	solutions.	This	is	to	say	that	the	expected	
energy	 savings	 that	 could	 be	 realized	 through	 day-to-day	 curtailment	 behaviours	 were	 perceived	
insignificant	 or	 low,	 when	 compared	 to	 the,	 perceived,	 saving	 potential	 that	 could	 be	 achieved	 through	
investments,	such	as	buying	energy	efficient	appliances,	investing	in	renewable	energy	sources,	or	even	by	
moving	into	a	different	house.	However,	the	majority	of	FGs’	participants	and	all	three	CID	interviewees	
were	 aware	 that	 realizing	 such	 outcome	 expectations,	 through	 efficiency	 behaviours,	 would	 require	
surpassing	a	set	of	financial	and	technical	barriers.	
A	second	reason	appears	to	relate	to	the	individual	effort	that	is	required	to	maintain	those	behaviours,	as	
well	as	to	promote	them	within	family	members.	This	seemed	to	be	in	particular	important	for	those	FGs’
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participants	and	CID	interviewees,	whose	family	members	were	not	supportive	with	regards	to	more	energy	
efficient	lifestyles	at	home.	During	the	FGs	and	the	CID	interviews,	a	number	of	examples	were	provided,	
such	as	the	use	of	TV	and	PlayStations,	or	leaving	lights	on,	once	not	in	use.	It	also	could	be	observed	that	
family	members	either	reinforced,	or	served	as	a	driving	force,	to	save	energy,	or	in	the	opposite	direction	
they	behaved	in	a	way	that	would	increase	energy	use.	These	different	points	of	view	hold	the	potential	to	
cause	stressful	situations	at	home	and	are	in	particular	evident	in	parent-child	relationships,	with	two	FGs’	
participants	 reporting	 threatening	 to	 adopt	 extreme	 measures,	 like	 switching	 warm	 water	 off,	 if	 their	
children	 spend	 too	 much	 time	 under	 the	 shower.	 Those	 FGs’	 participants	 and	 CID	 interviewees	 with	
unsupportive	family	members	reported	either	to	be	willing	to	make	an	additional	effort	to	convince	other	
family	members	to	use	less	energy,	or	to	just	accept	what	the	remaining	family	members	did	in	order	to	
avoid	conflict.		
This	feeling	of	being	alone	in	their	individual	efforts	to	save	energy	relates	to	the	third	observed	reason,	
unwillingness	to	adopt	more	energy	efficient	behaviours;	where	individual	efforts	were	perceived	as	having	
only	a	small	impact	and	that	they	would	require	a	collective	effort,	from	the	remaining	family	members,	as	
well	as	society	in	general.	The	majority	of	FGs’	participants	and	CID	interviewees	reported	believing	their	
behaviours	have	little	effect	impact	on	the	environment,	without	collective	effort.	This	is	mirroring	findings	
in	 Kaplan	 (2000),	 on	 the	 potential	 impact	 of	 one’s	 contribution	 and	 the	 perception	 of	 helplessness	 and	
personal	 sacrifice.	 During	 the	 FGs	 and	 the	 CID	 interviews,	 this	 feeling	 of	 being	 alone	 in	 their	 individual	
efforts,	was	often	reported	to	exist	within	the	participants’	households,	e.g.	between	partners	and	parents-
children	relationships,	but	also	with	the	majority	of	the	FGs’	participants,	who	reported	the	feeling	that	
saving	energy	is	not	a	widespread	practice	among	society.	For	this	reason,	doing	something	that	others	
were	 not	 doing	 was	 reported	 as	 a	 discouragement	 to	 their	 attempts	 to	 save	 energy,	 because	 singular	
activity	was	not	felt	to	be	worthwhile,	or	effective,	with	an	overall	tendency	for	FG	participants	to	ascribe	
the	 responsibility	 of	 saving	 energy	 to	 others,	 namely	 neighbours,	 local	 and	 national	 government	 or,	
perceived,	big	polluters,	such	as	industry:	
“Our	first	example	should	come	from	the	government.	If	they	don't	do	it,	(talking	about	saving	
energy),	why	should	we	do	it?”	Female,	FG7
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In	summary,	adopting	more	energy	efficient	behaviour	frequently	did	not	appear	to	be	a	question	of	ability,	
but	rather	of	willingness	of	doing	so	and	thus	relates	to	the	outcome	expectations,	such	as	the	expectations	
regarding	energy	savings	and	individual	impact,	or	contrarily,	the	perceived	negative	aspects,	such	as	loss	in	
comfort,	wellbeing	and	family	harmony.	
7.4 	Concluding	remarks	
This	chapter	discussed	the	findings	from	the	empirical	study	looking	at	what	influences	energy	use	at	home,	
(RQ2),	within	a	Portuguese	context.	
The	following	table	summarises	the	findings	from	the	research	presented	in	this	chapter.	These	are	related	
to	the	RQs	and	highlight	the	gaps	identified	by	the	empirical	studies.
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Table	7-2	–	Summary	of	findings	relating	to	RQ2.	
Empirical	study	findings	 RQ	 Noteworthy	further	observation	
Chapter	Section:	7.1.Relation	of	behaviours	and	energy	use	
Chapter	Section:	7.1.	Motivational	variables	and	energy	efficient	behaviours	
7.1.1.	The	motivation	for	saving	money	
Saving	 money	 as	 the	 most	 reported	 motivation	 to	 saving	
energy.	
RQ2a,	RQ2b	
There	appears	to	be	a	misconception	regarding	the	concept	of	saving,	with	saving	
energy	being	interpreted	as	saving	money.	
While	cost-savings	have	been	reported	as	the	most	important	
motivation,	 it	 could	 be	 equally	 observed	 that	 monetary	
motivation	appeared	to	be	in	direct	conflict	with	curtailment	
behaviours	 that	 would	 be	 required	 to	 actually	 realize	 such	
monetary	gains.	
RQ2a,	RQ2b	
The	motivation	to	save	for	monetary	reasons	seems	to	be	even	more	important	to	
those	that	appeared	to	have	a	lower	level	of	disposable	income.	
Direct	and	indirect	rebound,	with	financial	saving	being	used	in	
energy	 and	 carbon	 intensive	 behaviours,	 reducing	 the	
environmental	benefit	achieved	through	the	energy	saved.	
RQ2b	
Misconceptions,	in	terms	of	individual	behaviour,	that	could	save	energy	without	
necessarily	impacting	the	environment,	i.e.,	the	use	of	home	appliances	during	the	
off	peak	tariffs	and	the	use	of	wood	as	a	way	to	save	energy.	
7.1.2.	Pro-environmental	and	pro-social	motivations	
Positive	 attitudes	 towards	 energy	 saving	 seemed	 to	 be	
surpassed	 by	 the	 direct,	 individual,	 benefits	 of	 energy	 use,	
such	as	comfort	and	wellbeing.		
RQ2c	
In	isolation,	environmental	and	energy	conservation,	might	be	strong	motivational	
variables,	but	comparatively	weak	when	in	conjunction	with	other	variables	such	
as	comfort	and	convenience.	
Attitude-behaviour	gap:	pro-environmental	attitudes	seem	to	
have	little	predictive	power	to	explain	energy	use	at	home.	
RQ2c	
Understanding	 that	 today’s	 generation	 would	 not	 suffer	 the	 consequences	 of	
predicted	and	forthcoming	environmental	problems.
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Empirical	study	findings	 RQ	 Noteworthy	further	observation	
7.1.3.	Needs	and	expectations	and	its	relation	to	motivation	for	saving	energy	
Current	 energy	 use	 perceived	 as	 socially	 acceptable,	 with	
people’s	 behaviour	 aligned	 to	 what	 appears	 to	 be	 the	 social	
norm	 and	 expectations	 regarding	 the	 fulfilment	 of	 individual	
needs.	
RQ2b,	RQ2c	 		
Chapter	Section:	7.2.	Barriers	for	adopting	more	energy	efficient	behaviours	
7.2.1.	External/macro	barriers:	policy	based,	structural	and	economic	barriers	
Policy	 based	 barriers:	 need	 for	 product	 standardization	 and	
development	of	penalty/incentive	schemes.	
RQ2c	 		
Physical-structural	barriers:	infrastructure	of	the	house,	as	well	
as	existing	home	appliances.	
RQ2b,	RQ2c	 		
Evidence	of	the	lock	in	effect:	changing	existing	infrastructure	
will	be	cost	intensive	and	only	feasible	in	the	medium-term.	
RQ2b,	RQ2c	 		
Reduced	 availability	 to	 invest	 in	 more	 energy	 efficient	
solutions.	
RQ2b	 		
7.2.2.	Knowledge	based	barriers	
Lack	of	information,	as	the	most	commonly	reported	barrier	to	
save	energy	at	home.	
RQ2b	 Misconception	regarding	the	use	of	off	peak,	as	a	way	to	save	energy.
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Empirical	study	findings	 RQ	 Noteworthy	further	observation	
7.2.2.	Knowledge	based	barriers	(cont.)	
Existing	lack	of	information	with	regards	to:	(1),	overall	energy	
use,	 (2)	 the	 contribution	 of	 specific	 home	 appliances	 and	
behaviours	 to	 total	 amount	 energy	 use,	 (3),	 the	 amount	 of	
energy	 that	 can	 be	 saved	 by	 adopting	 more	 energy	 efficient	
behaviour.		
RQ2b,	RQ2c	
No	clear	understanding	of	how	far	this	lack	of	information	is	a	barrier	towards	the	
adoption	of	more	energy	efficient	behaviours.	There	seems	to	be	an	information-
behaviour	 gap	 and	 people	 do	 not	 act	 in	 accordance	 to	 their	 reported	 level	 of	
knowledge,	 but	 less	 certainty	 exists	 once	 looking	 at	 specific	 behaviours	 where	
there	appears	to	be	the	need	for	further	information.	
Apparent	difficulty	when	comparing	behaviour	and	in	understand	their	individual	
contribution	to	energy	savings.			
Acknowledged	difficulty	in	understanding	the	relation	between	individual	energy	
use	and	environmental	damage,	which	together	negatively	influenced	individual	
motivation	to	save	energy	(see	7.1.2).	
Strong	agreement	that	knowing	the	individual	contribution	of	energy	consuming	
behaviour	could	influence	the	adoption	of	more	energy	efficient	behaviour.	
Understanding	 of	 energy	 in	 monetary	 terms	 rather	 than	
energy	units,	which	increase	the	difficulty	of	understanding	the	
difference	in	energy	use	to	the	price	of	energy.	
RQ2b,	RQ2c	
No	 clear	 understanding	 whether	 denying	 to	 not	 being	 able	 to	 save	 energy,	 is	 a	
strategy	to	deny	personal	responsibility.	
The	understanding	of	normal	energy	use	is	required	for	better	
understanding	individual	energy	use.	
RQ2b,	RQ2c	 		
7.2.3.	Cultural-normative-social	barriers	
Cultural	 and	 social	 norms	 were	 perceived	 as	 influencing	 the	
normal	way	of	using	energy	at	home	and	as	such,	set	the	limits	
to	 change	 and	 adoption	 of	 more	 energy	 efficient	 behaviours	
and	practices	that	were	perceived	as	not	desirable.	
RQ2b,	RQ2c	 		
Adopting	 more	 energy	 efficient	 behaviours	 might	 challenge	
existing	ways	of	thinking	and	behaving:	the	social	customs	and	
the	way	of	living.	
RQ2b,	RQ2c	 		
Social	 norm	 seems	 to	 accept	 a	 level	 of	 energy	 use,	 without	
being	perceived	as	overuse.	
RQ2b,	RQ2c
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Empirical	study	findings	 RQ	 Noteworthy	further	observation	
Chapter	Section:	7.3.	Individual	psychological	factors	as	a	barrier	
7.3.1.	Habits	as	an	obstacle		
Most	energy	related	behaviours	are	of	a	habitual	nature	and	
acquired	over	time.	
RQ2b,	RQ2c	 		
Reasons	for	adopting	more	energy	efficient	habits	as	hard	to	
achieve	 include:	 (1),	 remembering	 to	 do	 the	 right	 thing,	 (2),	
habits	provide	a	level	of	comfort,	convenience	and	well-being	
that	 allows	 for	 lazy	 and	 self-indulgent	 behaviour,	 (3),	
scepticism	 regarding	 the	 impact	 of	 these	 habits	 in	 terms	 of	
home	energy	use.	
RQ2b,	RQ2c	
Early	influences	on	energy	use	appeared	to	be	critical	in	developing	habits	that	are	
learnt	and	embedded.	
7.3.2.Comfort	and	convenience	
Saving	 money,	 or	 the	 environment,	 enters	 into	 competition	
with	comfort	and	convenience.	
RQ2b,	RQ2c	 		
Overall	 tendency	 for	 considering	 family	 wellbeing	 as	 more	
important	 than	 the	 financial,	 or	 environmental,	 impact	 of	
saving	energy.	
RQ2b,	RQ2c	 		
7.3.3.Efficacy	and	outcome	expectations	
Good	 reported	 levels	 of	 overall	 efficacy	 expectations,	 with	
different	 efficacy	 expectations	 depending	 on	 the	 behaviour	
under	discussion.	
RQ2b,	RQ2c	 		
Low	level	of	outcome	expectations,	not	only	with	regard	to	the	
amount	of	energy	that	can	be	reduced,	as	well	as	the	need	for	
collective	effort	in	order	to	be	meaningful.	
RQ2b,	RQ2c	
Feeling	 of	 helpless	 and	 ineffectiveness	 of	 one’s	 own	 contribution	 that	 start	 at	
home,	since	it	was	often	reported	to	be	an	individual	effort	and	not	shared	by	all	
family	members,	which	reduced	even	further,	the	attempts	to	save	energy	within	
the	household	level	unit.	
Reporting	 to	 already	 act	 in	 a	 more	 energy	 efficient	 way,	
apparently	 provides	 a	 feeling	 of	 indulgence	 that	 justifies	 a	
perception	of	no	need	for	further	action.	
RQ2b,	RQ2c	 		
Efficacy	 increases	 for	 easy	 to	 do	 things	 that	 have	 no	 real	
impact	on	comfort	and	wellbeing	levels.	
RQ2b,	RQ2c
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Empirical	study	findings	 RQ	 Noteworthy	further	observation	
7.3.4.Resistence	and	unwillingness	to	change	
Resistance	 to	 and	 unwillingness	 to	 change	 often	 appear	 to	
result	 from:	 (1),	 low	 outcome	 expectancy,	 associated	 with	
curtailment	behaviour,	(2),	individual	effort	that	is	required	to	
maintain	those	behaviours,	as	well	as	to	promote	them	within	
the	 family	 members	 and	 (3),	 individual	 efforts	 perceived	 as	
having	a	small	impact,	that	would	require	a	collective	effort,	
from	the	remaining	family	members,	as	well	as	society.	
RQ2b,	RQ2c	
Findings	suggest	that	adopting	more	energy	efficient	behaviour	doesn’t	appears	to	
be	 a	 question	 of	 ability,	 but	 rather	 of	 willingness	 of	 doing	 so,	 which	 relates	 to	
outcome	 expectations,	 both	 in	 terms	 of	 energy	 saved,	 as	 well	 as	 the	 need	 for	
collective	action.
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As	can	be	seen	from	this	chapter,	the	barriers	reported	within	the	energyprofiler	survey	questionnaire,	(EP),	
focus	groups,	(FGs)	and	in-depth	individual	interviews,	(ID),	outnumbered	motivations	to	reducing	energy	
use	at	home.	In	addition	to	this,	the	motivations	that	have	been	presented	did	not	appear	to	result	in	actual	
energy	use	reductions.	Positive	attitudes	towards	energy	saving,	appeared	to	be	surpassed	by	the	individual	
direct	benefits	of	energy	use,	such	as	comfort	and	wellbeing.	Equally,	monetary	motivation	appeared	to	be	
in	 direct	 conflict	 with	 curtailment	 behaviours	 that	 would	 be	 required	 to	 actually	 realize	 such	 monetary	
gains.	Thus,	motivational	variables	appeared	to	be	in	direct	competition	with	the	barriers,	such	as	reduced	
convenience	and	comfort.	These	findings	support	well	the	literature	that	had	been	presented	in	chapter	3	
and	 thus	 support	 earlier	 results	 from	 Barenergy	 (2011),	 Darnton	 (2008),	 Darnton	 et	 al.	 (2011),	 Jackson	
(2005)	and	Prendergrast	et	al.	(2008).	
The	 results	 do	 show	 however,	 that	 reported	 barriers	 are	 perhaps	 not	 actual	 barriers,	 but	 in	 part	 a	
convenient	 excuse,	 exemplified	 by	 the	 information-behaviour	 gap,	 (Jackson,	 2005;	 Schultz,	 2002;	
Southerton	et	al.,	2011;	Stern,	1999)	This	supports	the	earlier	findings	from	Baker	and	Kirsch	(1991),	that	
people	tend	to	verbalize	an	inability	to	do	something,	as	a	way	of	denying	personal	responsibility	in	dealing	
with	a	problem.	This	could	also	be	observed	with	regards	to	efficacy	and	outcome	expectations,	which	as	
such,	did	not	appear	to	be	a	major	barrier.	Notably,	the	findings	from	the	FGs	showed	that	the	question	is	
perhaps,	less	about	being	able	to	adopt	more	energy	efficient	behaviours	and	more	about	the	willingness	to	
do	so.	Thus,	the	overall	results	from	this	chapter	reflect	the	literature	findings	presented	in	chapter	3.
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8 	Intervention	strategies	and	perceived	effectiveness	
Chapter	 eight	 explores	 the	 perceived	 effectiveness	 of	 different	 intervention	 strategies	 and	 the	 potential	
effectiveness	of	change	interventions	within	the	 field	of	energy	use	at	home.	The	chapter	discusses	the	
findings	 from	 the	 energyprofiler	 survey	 questionnaire,	 (EP),	 the	 focus	 groups,	 (FGs)	 and	 the	 in-depth	
individual	 interviews,	 (ID),	 regarding	 the	 findings	 on	 the	 role	 of	 intervention	 strategies	 in	 energy	 use	 at	
home,	(RQ3).		
Intervention	 strategies	 and	 their	 perceived	 effectiveness,	 in	 encouraging	 the	 adoption	 of	 more	 energy	
efficient	behaviour,	were	initially	explored	during	the	FGs,	with	participants	being	asked	to	propose	specific	
interventions	 that	 could	 be	 launched	 nation-wide	 in	 order	 to	 encourage	 the	 adoption	 of	 more	 energy	
efficient	behaviour	at	home.	The	topic	was	further	explored,	within	the	CID	and	PID	interviews,	in	order	to	
better	understand	what	future	interventions	might	look	like.	Figure	8-1,	shows	the	type	of	interventions	
discussed	during	roundtable	discussions	and	how	FGs’	participants	perceived	that	these	interventions	could	
address	barriers	to	the	adoption	of	more	energy	efficient	behaviour	at	home.	Data	regarding	the	types	of	
intervention	have	been	extracted	from	FGs’	transcripts,	with	follow	up	discussion	identifying	barriers	where	
intervention	could	be	addressed.		
	
Figure	8-1:	Type	of	interventions	in	relation	to	the	barriers	that	could	be	addressed.	
Type	of	Intervention FG1 FG2 FG3 FG4 FG5 FG6 FG7
Monitoring	systems	(e.g.	energymeters) .. .. ... . ... ...
Education	 . . .. .. . .. ..
Prompting .. .. .. ..
Benefit	vs.	Penalty	 .. . . ... ..
Provision	of	financial	incentives .. . . .
Provision	of	simple	comparative	terms	(e.g.	home	appliance) . .. ..
Comparison	to	other	people . .
Provision	of	general	information	on	how	to	save	energy	at	home . . . . . . .
Provide	an	average,	normal	energy	use	value ... ... ... ...
Demonstrate	good	practices/Model	behaviours ... ... . .. ..
Inclusion	of	smart	features	in	the	home	appliances . . .
Provision	of	simple	examples	at	the	energy	invoices .. .
Provision	of	information	at	the	point	of	sales . . . .
Provision	of	tailored	information	(e.g.	energy	audit) .. .. . ..
Provision	of	free	samples . . . . . . .
Labelling	of	products .. .. .. ... ..
Barriers:	Inability	to	measure	energy	use|Lack	of	information|Initial	investment	cost	|	Habit	|	Invisibility	|	Social	norms
8.	Intervention	strategies	and	perceived	effectiveness	
	
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As	 can	 be	 seen	 from	 Figure	 8-1,	 education,	 provision	 of	 general	 information,	 or	 the	 provision	 of	 free	
samples,	 have	 been	 put	 forward	 by	 each	 of	 the	 7	 FGs	 as	 suitable	 interventions.	 Similarly,	 the	 use	 of	
monitoring	 systems,	 benefit	 vs.	 penalty	 type	 schemes,	 demonstration	 of	 good	 practice,	 as	 well	 as	 the	
provision	of	tailored	information,	including	labelling	of	products,	were	seen	by	FGs’	participants	as	possible	
interventions	 that	 hold	 high	 potential	 for	 encouraging	 the	 adoption	 of	 more	 energy	 efficient	 behaviour.	
These	will	be	looked	at	more	in	detail	through	this	chapter.	Further,	as	can	be	seen	from	Figure	8-1,	FG1,	
FG4	 and	 FG5	 are	 minimally	 populated,	 in	 terms	 of	 type	 of	 interventions	 discussed,	 when	 compared	 to	
others.	This	could	only	be	seen	while	compiling	the	data	and	as	such,	the	reasons	for	this	have	not	been	
directly	 explored	 within	 the	 FGs.	 However,	 each	 FG	 had	 specific	 characteristics,	 with	 FG1	 composed	 of	
participants	 that	 work	 within	 the	 energy	 efficiency	 field,	 that	 hold	 a	 consistent	 opinion	 regarding	 the	
effectiveness	of	the	different	types	of	intervention.	This	might	be	a	reason	for	them	discussing	a	reduced	
number	of	intervention	types,	that	they	perceived	as	most	effective	and	worthy	of	mention.	Regarding	FG4	
and	FG5,	participants	seemed	to	hold	a	lower	purchasing	power,	as	well	as	a	lower	education	level,	which	
may	 contribute	 to	 a	 reduced	 set	 of	 intervention	 alternatives	 that,	 in	 particular,	 target	 the	 financial	
component	of	energy	use.	
In	this	chapter,	the	nature	of	Intervention	strategies	discussed	by	research	participants	and	their	perceived	
effectiveness,	will	be	presented	in	more	detail.	
8.1 	Communication	design	and	persuasion	
As	can	be	seen	from	the	literature,	persuasion	can	influence	others,	(Jackson,	2005;	Martiskainen,	2007;	
Simons,	1976,	p.	21)	and	is	often	dependent	on	the	credibility	of	the	sender,	the	persuasiveness	of	the	
argument/message,	 or	 the	 responsiveness	 of	 the	 audience,	 (O’Keefe,	 1990).	 Thus	 persuading	 people	 to	
change	 can	 be	 particularly	 difficult,	 (Jackson,	 2005).	 Therefore,	 one	 objective	 of	 the	 FGs	 was	 to	 further	
explore	 the	 perceived	 requirements	 for	 communication	 design	 and	 persuasion.	 FGs’	 participants	 were	
asked	to	recall	campaigns	promoting	energy	efficient	behaviour	and	subsequently,	were	asked	to	design,	
for	 themselves,	 a	 communication	 and	 information	 campaign	 on	 how	 to	 promote	 the	 adoption	 of	 more	
energy	efficient	behaviour.
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With	regards	to	communication	design,	in	four	of	the	FGs	the	general	importance	of	the	message	sender	
was	stressed	and	that	they	need	to	be	both	reliable	and	able	to	create	empathy	with	the	targeted	audience.	
The	FGs’	roundtable	discussion	brought	up	a	number	of	examples	of	what	could	be	considered	a	reliable	
and	persuasive	sender,	with	overall	agreement	towards	ordinary	people,	known	actors	or	TV	reporters	and	
children.	Messages	issued	by	utility	companies	were	considered	helpful,	but	potentially	less	effective	since	
they	could	lead	to	confusion	and	distrust.	FGs’	participants	pointed	out	confusion	when	receiving	advice	
from	 their	 electricity	 supplier	 to	 save	 energy,	 as	 this	 was	 perceived	 as	 reducing	 their	 own	 business.	 In	
addition	 to	 this,	 it	 was	 stressed	 that	 the	 message/argument	 needs	 to	 be	 persuasive,	 in	 order	 not	 to	 be	
rejected	 or	 ignored,	 as	 a	 way	 to	 avoid	 confronting	 implications	 for	 appreciated	 energy	 inefficient	
behaviours,	as	postulated	by	Upham	et	al.,	(2009).		
Further	 to	 this,	 an	 overall	 agreement	 could	 be	 seen	 among	 the	 majority	 of	 FGs’	 participants	 and	 ID	
interviewees,	that	persuading	people	to	adopt	more	energy	efficient	behaviour	would	be	challenging	to	
achieve,	 in	 particular	 for	 less	 easy,	 or	 simple	 behavioural	 changes	 or,	 those	 that	 were	 perceived	 as	
impacting	desired	normal	levels	of	comfort,	convenience	or	wellbeing.	It	could	not	be	found	however	if	
messages	promoting	such	undesired	and	unpopular	energy	efficient	behaviours	could	actually	not	backfire	
and	 highlight	 the	 prevalence	 of	 energy	 inefficiency	 as	 a	 habit	 shared	 by	 other	 people.	 This,	 apparent,	
individual	unwillingness	to	address	comfort	and	wellbeing	levels	was	shared	across	FGs’	participants,	CID	
and	PID	interviewees	and	it	is	uncertain	how	successful	future	interventions	could	be	that	target	such	a	
focus.	 Findings	 from	 this	 research	 suggest	 rather	 that	 promoting	 the	 adoption	 of	 more	 energy	 efficient	
behaviour,	perceived	as	having	undesirable	consequences,	could	lead	people	to	not	doing	so.	This	situation	
is	known	in	the	literature	as	a,	‘confirmation	bias’	where	people	look	for	information	that	is	consistent	with	
what	they	already	think,	want,	or	feel,	leading	them	to	avoid,	dismiss,	or	forget	information	that	will	require	
them	to	change	their	mind-set	and,	quite	possibly,	their	behaviour,	(Shome	&	Marx,	2009);	where,	“I	can’t”,	
simply	means,	“I	don’t	want	to”.	Findings	from	the	FGs	and	IDs	overall	suggest	that	an	individuals’	positive	
attitudes	towards	comfort	and	wellbeing,	are	stronger	than	attitudes	towards	the	environment	and	as	such,	
there	might	not	be	any	emotions,	such	as	disappointment,	dissatisfaction,	shame,	embarrassment	or	guilt,	
that	 could	 help	 lead	 to	 the	 adoption	 of	 more	 energy	 efficient	 behaviour.	 Therefore,	 interventions	 that	
would	draw	from	persuasion	theories,	(section	4.	2)	and	that	use	judgment,	cognitive	dissonance	or	self-
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discrepancy	methodologies	would	not	be	perceived	as	persuasive,	or	potentially	effective,	with	regards	to	
triggering	the	desired	response	from	the	audience.		
8.2 Structural	interventions		
8.2.1 	Rewards	and	punishments	
A	rewards	and	punishment	scheme	was	discussed	within	five	out	of	the	seven	FGs	as	a	way	to	encourage	
the	adoption	of	more	energy	efficient	behaviour.	FGs’	participants	were	found	open	to	an	approach	that	
would	reward	those	people	who	underused	energy	and	punished	those	that	over	used	it.	As	a	pre-requisite	
for	such	a	scheme,	FGs’	participants	agreed	on	the	need	to	define	a	set	of	base	values	for	energy	use	at	
home,	to	punish	those	overusing	and	reward	those	underusing	energy	at	home.	In	accordance	with	FGs’	
participants,	a	base	value	for	energy	use	should	take	into	account	the	amount	of	energy	required	to	fulfil	
basic	needs;	though	it	was	not	fully	understood	what	was	considered	to	be	a	basic	need	and,	similar	to	the	
discussions	 of	 chapter	 six	 and	 seven,	 what	 is	 understood	 to	 be	 normal.	 Some	 of	 the	 FGs’	 participants	
suggested	this	base	level	of	energy	use	could	be	provided,	either	for	free,	or	at	a	flat	rate	entrance	value,	so	
as	to	provide	an	understanding	of	what	is	considered	an	acceptable	level	of	basic	energy	use	at	home.	This	
concept	of	a	flat	basic	and	an	increasing	non-basic	rate	was	compared	by	some	of	the	FGs’	participants	with	
one	that	they	recalled	for	water	consumption	in	Portugal,	where	people	paid	different	prices	for	water,	
higher	consumption	equalling	a	higher	price	charged.	Yet,	even	though	greeted	by	initial	enthusiasm	from	
the	roundtable	discussion	during	FGs,	it	was	not	possible	to	determine	how	effective	such	a	scheme	could	
be.		
A	number	of	FGs’	participants	expressed	an	opinion	that	such	a	scheme	would	probably	not	work,	due	to	a	
lack	of	motivation	and	that	people	would	maintain	established	practices	as	long	as	they	could	afford	to	use	
energy	 as	 they	 do	 at	 the	 present.	 Despite	 such	 concerns,	 there	 was	 an	 overall	 agreement	 that	 such	 a	
scheme	should,	nevertheless,	facilitate	the	development	of	a	measurable	mind	set	for	energy	use,	as	well	as	
being	a	fair	instrument	to	compensate	those	people	willing	to	adopt	more	energy	efficient	behaviour	and	to	
use	less	energy	at	home.	In	contrast	to	FGs’	participants,	PID	interviewees	did	not	consider	such	scheme	a	
viable	intervention,	although	each	for	different	reasons.	In	PID1,	the	interviewee	from	an	energy	supplier,
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argued	 that	 such	 a	 scheme	 could	 backfire	 since	 there	 is,	 currently,	 no	 value	 to	 identify	 what	 a	 normal,	
(average),	 use	 of	 energy	 could	 be,	 as	 well	 how	 to	 best	 calculate	 such	 value,	 which	 could	 be	 a	 complex	
process	to	implement	and	monitor.	With	PID2,	the	interviewee	from	the	national	energy	agency	argued	
that	people	can	only	support	penalties	and	punishments	until	a	certain	point	and	that	the	energy	saved	
should	be	motivation	enough	to	adopt	more	energy	efficient	behaviour.	For	PID3,	the	interviewee	from	the	
national	utility	program,	preferred	to	promote	adoption	of	long-term	mechanisms	that	support	a	consistent	
reduction	of	energy	demand,	rather	than	random	measures	focused	on	specific	scenarios.	
In	summary,	results	from	this	research	suggest	that	energy	users	and	intervention	providers	have	different	
opinions	regarding	the	use	of	reward	and	punishment	intervention	schemes.	From	a	user	point	of	view,	
reward	 and	 punishment	 schemes	 appear	 to	 be	 evaluated	 as	 desirable	 and	 a	 partially	 effective	 type	 of	
intervention.	While	from	an	intervention	provider	this	intervention	type	does	not	seem	to	be	that	appealing	
or	perceived	as	effective.		
8.2.2 	Incentives	and	samples	
The	provision	of	incentives,	including	samples	of	more	energy	efficient	home	appliances,	was	evaluated	as	
an	effective	alternative	to	promoting	the	adoption	of	more	energy	efficient	technologies,	by	removing	or	
reducing	the	risk	energy	users	would	need	to	take.	The	provision	of	samples	was	discussed	within	all	7	FGs,	
with	FGs’	participants	providing	the	example	of	energy	efficient	light	bulbs	that	were	distributed,	for	free,	
as	part	of	a	national	program	to	reduce	the	market	entrance	barriers	to	the	deployment	of	the	new	light	
bulb	technologies
15
.	FGs’	participants	agreed	that	this	distribution	of	light	bulbs,	for	free,	allowed	them	to	
experiment	and	removed	the	burden	of	investment	for	such	initial	experimentations.	In	addition	to	this,	
FGs’	participants	also	highlighted	the	low	personal	effort	that	was	required	to	get	their	sample	light	bulb:	
“One	only	needed	to	exchange	the	light	bulbs…they	even	sent	one	to	home”,	Male,	FG7	
“I	got	them	for	free,	it	was	a	bonus…	they	were	giving	them	away	at	the	supermarket”,	Male	
FG4	
																																																																				
15
	The	distribution	of	more	energy	efficient	appliances	was	financed	through	a	Portuguese	National	Fund	aiming	at	promoting	energy	
efficiency	within	the	residential,	services	and	industry	sectors.	More	information	available	at	www.erse.pt
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Based	on	such	positive	experience,	FGs’	participants	suggested	that	the	government	could	promote	similar	
interventions	for	other	home	appliances,	as	well	as	renewable	energy	sources,	as	a	way	to	reduce	the	initial	
investment	required	in	purchasing	more	energy	efficient	appliances.	Even	though	there	were,	at	that	time,	
other	 type	 of	 financial	 incentives	 to	 adopt	 more	 energy	 efficient	 home	 appliances	 or	 renewable	 energy	
sources,	only	a	reduced	number	of	FGs’	participants	were	aware	of	such	incentive	schemes.	
Within	 subsequent	 PID	 interviews,	 interviewees	 were,	 nevertheless,	 reluctant	 towards	 such	 types	 of	
intervention,	 with	 two	 out	 of	 three	 interviewees	 criticizing	 the	 unfairness	in	 distribution	 that	 frequently	
accompanies	 the	 sample,	 or	 incentive	 provision.	 As	 a	 concrete	 example,	 PID2	 referred	 to	 the	 energy	
efficient	light	bulbs,	where	the	criterion	of	receiving	one	was	to	have	lower	average	bills,	resulted	in	light	
bulbs	being	repositioned	to	holiday/second	homes.	In	addition	to	the	unequally/unfair	distribution,	PID3	
had	a	general	concern	that	supplying	energy	efficient	appliances,	for	free,	could	promote	the	introduction	
of	more	energy	efficient	products	that	are	at	an	early	stage	of	technological	maturity,	which	could	lead	to	a	
lost	opportunity	of	promoting	the	technology	in	the	future,	if	the	first	user	experience	is	negative.	
8.2.3 	Labelling	
During	the	FGs’	roundtable	discussion,	a	frequent	narrative	emerged,	centered	around	the	discussion	of	A	
rated	home	appliances	being	better	than	others.	Nevertheless,	during	FG1,	those	participants	working	in	
the	energy	area,	suggested	that	people	in	general	do	not	understand	the	scope	of	energy	rating	labels,	are	
unable	to	compare	the	performance	of	different	home	appliances	and	that	as	a	result,	they	do	not	know	
how	much	energy	they	will,	potentially,	consume,	or	save.	This	view	was	common	across	the	other	FGs	in	
two	different	ways.	First	of	all,	during	the	FGs	there	was	no	discussion	comparing	other	characteristics	such	
as	 size,	 load	 capacity,	 or	 use	 pattern,	 that	 influence	 the	 amount	 of	 energy	 used	 and	 that	 would	
demonstrate	 FGs’	 participants	 understanding	 the	 impact	 of	 their	 purchasing	 decision.	 Rather	 than	
questioning	if	one	needs	a	bigger	fridge	or	washing	machine,	the	notion	was	that	as	long	as	it	is,	‘A	rated’,	it	
is	energy	efficient	and	as	such,	it	is	a	good	purchase.	Secondly,	a	few	of	the	FGs’	participants	recommended	
that	 all	 non	 A-rated	 home	 appliances	 should	 be	 banned	 from	 the	 market	 as	 an	 alternative,	 to	 release	
consumers	from	the	need	of	trying	to	compare	the	different	available	options.	During	the	FGs	it	was	not	
possible	to	fully	understand	if	this	was	a	strategy	to	promote	sustainability,	or	rather	translating	into	the
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difficulty	FGs’	participants	might	have	in	understanding	the	information	provided	by	the	labels,	though	it	
could	equally	have	been	an	example	for	choice	architecture,	as	will	be	further	discussed	in	section	8.2.5.	
Findings	 do,	 however,	 question	 the	 effectiveness	 of	 labels.	 Even	 though	 labels	 apparently	 provided	
meaningful	and	easy	to	understand	information,	it	was	not	clear	that	the	use	of	standardized	labels	across	
products	would	indeed	lead	to	better	informed	purchasing	decisions	and,	in	particular,	for	those	consumers	
that	lack	motivation	and	knowledge	to	compare	different	solutions,	in	terms	of	purchase	and	later	use.	This	
might	be	one	of	the	reasons	for	some	FGs’	participants	reporting	looking	for	information	at	the	point	of	
sale,	 as	 well	 as	 from	 the	 shop	 staff.	 Shop	 staff	 appeared,	 during	 the	 FGs	 and	 the	 CID	 interviews,	 to	 be	
perceived	 as	 a	 trusted	 source	 of	 information	 to	 facilitate	 the	 purchase	 of	 more	 energy	 efficient	 home	
appliances	 instead	 of,	 or	 in	 combination	 with,	 energy	 labels.	 One	 PID	 interviewee	 even	 extended	 the	
discussion	 to	 the	 home	 energy	 performance	 certificate
16
,	 an	 energy	 label	 for	 homes	 and	 questioned	
whether	people	would	pay	much	attention	to	the	energy	class	of	the	house,	or	whether	other	variables	
would	be	of	a	higher	relevance	to	the	buyer,	such	as	the	house	location.	The	PID	interviewee	questioned	
the	impact	of	such	a	certification	due	to,	their,	individual	understanding	that	people	mainly	request	the	
certificate	to	comply	with	the	law	if	they	want	to	sell/rent	a	house,	rather	than	being	interested	in	and	
motivated	to	adopting	the	efficiency	measures	proposed	within	the	certificate.		
In	summary,	results	suggest	that	labels	could	be	an	adequate	intervention	type;	though	it	equally	appears	
that	an	increased	level	of	knowledge	might	be	required	to	understand	the	information	within	such	labels.	
Findings	also	indicate	that	it	was	not	understood	that	the	A	label	alone	is	only	a	relative	indicator	and	not	to	
be	seen	in	isolation	from	the	actual	day	to	day	usage.	Analogous	to	the	literature,	findings	did	indicate	that	
it	might	thus	be	a	requirement	to	provide	a	consistent	and	comparative	level	of	information	for	consumers,	
(DGGE/IP-3E,	2004).	With	this,	findings	show	that	the	general	challenge	for	labels	was	seen	to	be	to	ensure	
that	the	information	provided	is	meaningful,	easy	to	understand	and	standardised.	Also	that	consumers	are	
motivated	into	wanting	to	take	action	and	thus	supporting	earlier	findings	from	Southerton	et	al.,	(2011).	
	
																																																																				
16
	 Energy	 Performance	 Certificate	 are	 today	 obligatory	 for	 homes	 under	 the	 Energy	 Performance	 of	 Buildings	 Directive	 -	 Directive	
2002/91/EC,	EPBD.
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8.2.4 	Demonstrating	and	facilitating	
During	roundtable	discussions,	FGs’	participants	often	referred	to	modelling	and	demonstration	as	a	way	to	
promote	individual	behavioural	change.	FGs’	participants	discussed	three	situation	that	could	be	framed	
within	modelling	and	demonstration:	(1),	central/local	government	actions,	that	demonstrate	saving	energy	
is	 an	 important	 thing	 to	 do,	 for	 instance,	 by	 switching	 street	 or	 monument	 lights	 off	 at	 night;	 (2),	 the	
modelling	effect	of	parents	on	children,	and	vice	versa.	Behaviour	adopted	within	the	family	home	during	
childhood	seem	to	remain	into	adult	life	and,	in	contrast,	parents	are	influenced	by	their	children	and	the	
good	practices	they	learn	at	school,	(e.g.	with	the	recycling	practices);	(3),	demonstration	of	the	benefits	of	
more	energy	efficient	appliances.	Some	FGs’	participants	recalled	having	seen	a	comparison,	at	a	point	of	
sale,	 between	 traditional	 light	 bulbs	 and	 more	 energy	 efficient	 ones,	 placed	 side-by-side	 with	 an	
independent	 energy	 counter	 attached	 to	 each,	 indicating	 what	 amount	 of	 energy	 was	 being	 used.	 FGs’	
participants	 agreed	 that	 this	 allowed	 them	 to	 compare	 the	 individual	 energy	 consumption	 of	 each	
technology,	allowing	them	to	have	better	informed	decisions	in	a	very	easy	way:	
“They	had	a	traditional	light	bulb	on	with	the	counter	moving	and	next	to	it	an	energy	efficient	
one	with	the	counter	moving	much	slower	and	one	could	see	it”	Female,	FG7	
Findings	from	this	research	suggest	that	modelling	and	demonstration	was	perceived	to	be	an	effective	type	
of	 intervention,	 with	 regards	 to	 the	 provision	 of	 desirable	 behaviours	 and	 to	 encourage	 learning	 by	
observing	 how	 others	 behave.	 Modelling	 behaviour	 was	 also	 seen	 as	 a	 potentially	 effective	 avenue	 for	
changing	 behaviour,	 as	 people	 follow	 these	 examples	 once	 they	 are	 understandable,	 relevant,	 and	
rewarding	in	terms	of	positive	results.
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8.2.5 	Intervention	through	design	
During	the	FGs,	participants	discussed	two	types	of	intervention	with	regards	to	environmental	design	and	
material	context	adjustment.	Firstly,	the	need	to	change	home	infrastructure	and	appliances	towards	more	
energy	 efficient	 ones	 and	 secondly,	 the	 inclusion	 of	 smart	 features,	 which	 was	 perceived	 as	 a	 type	 of	
communication/feedback	mechanism	that	could	facilitate	using	home	appliances	more	efficiently	
With	regards	to	home	infrastructure,	FGs’	participants	and	ID	interviewees	highlighted	the	fact	that	the	
infrastructure	of	their	current	homes	is	not	supportive	towards	using	less	energy	without	having	to	trading-
off	their	present	level	of	comfort.	When	asked	to	evaluate	their	current	level	of	energy	use	and	comfort,	
and	to	forecast	for	the	10	years,	all	three	CID	interviewees	agreed	they	would	maintain,	or	increase,	their	
comfort	level,	whilst	potentially	reducing	energy	use	by	the	deployment	of	more	energy	efficient	appliances	
and	improved	home	infrastructure.	This	10-year	period	was	perceived	as	sufficient	to	improve	their	homes	
and	 to	 substitute	 existing	 home	 appliances	 with	 more	 energy	 efficient	 ones,	 which	 would	 lead	 to	 a	
potentially	reduced	level	of	energy	use	without	needing	to	take	additional	measures.	Yet,	regarding	energy	
related	practices,	interventions	that	were	put	forward	rather	focused	on	improving	home	infrastructure,	or	
existing	home	appliances,	in	order	to	promote	increased	savings,	but	largely	neglected	interventions	aimed	
at	how	the	home	and	home	appliances	are	used,	and	on	the	impact	of	everyday	behaviour	as	a	way	to	
reduce	energy	use.		
With	regards	to	the	way	products	are	designed	and,	in	particular,	the	inclusion	of	smart	features	that	could	
facilitate	the	adoption	of	more	energy	efficient	behaviours	at	home,	some	examples	were	provided	by	FGs’	
participants,	 such	 as	 the	 inclusion	 of	 sound	 alerts	 that	 would	 remind	 people	 to	 switch	 appliances	 off,	
comparing	this	to	the	system	recent	cars	have	to	remind	you	of	the	need	to	use	the	seat	belt.	This	connects	
with	the	literature	on	choice	architecture,	(Dobson,	2011;	Grist,	2010;	Southerton	et	al.,	2011;	Thaler	&	
Sunstein,	 2008),	 which	 from	 a	 product	 perspective	 could,	 for	 instance,	 mean	 only	 having	 a	 cold	 wash	
washing	 machine,	 rather	 than	 trying	 to	 educate	 people	 to	 wash	 at	 30º.	 Under	 these	 circumstances	 the	
home	 appliance	 itself	 would	 take	 the	 decision	 away	 from	 the	 user.	 FGs’	 participants	 used	 the	 standby	
option	as	a	way	to	express	how	convenient	and	comfortable	some	of	the	default	options	are	day-to-day:
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“I	try,	but	I	have	to	recognize	it’s	difficult	for	me	to	switch	appliances	from	standby.	For	
example,	we	are	in	bed	and	it’s	much	easier	to	switch	the	TV	with	the	remote	control…it’s	
more	comfortable…sometimes	I	remember	but	I’m	feeling	so	good	in	bed	that	I	don’t	stand	
up”,	Female,	FG6	
Within	subsequent	PID	interviews	and,	perhaps	a	bit	unexpectedly,	PID	interviewees	did	not	consider	such	
strategies	 that	 relate	 to	 choice	 architecture	 and	 the	 concept	 of	 nudging,	 (Dobson,	 2011;	 Grist,	 2010;	
Southerton	et	al.,	2011;	Thaler	&	Sunstein,	2008)	and	where	the	default	options	are	set	in	order	to	facilitate	
individual	best	practice.	The	reason	for	such	non-considerations	did	remain,	however,	unclear.	
In	summary,	findings	from	this	research	suggest	that	product	design	and	contextual	adjustments	could	be	
an	effective	type	of	intervention	to	reduce	energy	use	at	home,	but	that	they	will	not	necessarily	encourage	
the	adoption	of	more	energy	efficient	behaviours	as	such	as	they	are	based	on	a	‘technofix’	approach,	(see	
2.2.7,	4.3.2).	They	are	perceived	as	being	sufficient	and	thus	release	users	from	the	daily	effort	to	adopt	
more	energy	efficient	behaviour.	Adapting	product	design	seems	to	inhibit	the	potential	for	learning	and	
adopting	other	energy	efficient	behaviours,	other	than	that	relating	to	the	adopted	product.		
8.3 	Psychological	interventions	
8.3.1 Targeted	face-to-face	information		
During	the	FGs,	an	overall	agreement	could	be	observed	with	regards	to	advantages	of	providing	tailored,	
preferably	face-to-face,	information	and	feedback.	To	illustrate	the	point,	FGs’	participants	often	described	
a	scenario	where	someone	with	knowledge	in	the	area	would	visit	their	home,	evaluates	their	energy	use,	
and	then	provide	tailored	advice	on	how	they	could	save	energy	and	on	how	to	account	for	those	savings.	
Though	often	not	referring	to	the	technical	term,	FGs’	participants	were	describing	a	home	audit	as	a	means	
with	 significant	 potential	 for	 promoting	 energy	 saving	 at	 home.	 The	 main	 disadvantage	 of	 this	 type	 of	
intervention	relates,	however,	to	the	time	required	for	such	audits	and	the	inherent	cost	resulting	from	
being	 human	 resource	 intensive,	 (section	 4.4).	 Providing	 customized	 information,	 through	 a	 number	 of	
alternatives,	was	perceived	by	FGs’	participants	as	beneficial	to	better	understand	what	one	could	do	and
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how	 much	 energy	 could	 be	 saved	 for	 the	 specific	 individual	 circumstances,	 thus	 reducing	 the	 confusion	
between	the	amount	of	information	currently	available	and	the	difficulty	to	sort	out	what	is	important.	FGs’	
participants	reported	difficulty	in	understanding	the	available	information,	comparing	the	different	sources	
of	data,	as	well	as	being	able	to	reserve	time	for	doing	so.	Managing	and	understanding	existing	information	
was	often	perceived	as	over-demanding	for	the	majority	of	the	FGs’	participants,	since	it	requires,	time,	a	
degree	 of	 skill,	 and	 a	 willingness	 to	 do	 so.	 These	 findings	 suggest	 an	 overall	 concern	 regarding	 which	
information	is	accurate,	who	to	trust	in	the	myriad	of	actors	in	the	field,	from	utility	companies	to	NGOs	to	
suppliers	 of	 energy	 efficient	 products	 and	 services,	 crowned	 by	 a	 simultaneous	 lack	 of	 a	 reliable	 voice,	
without	vested	interest,	in	the	field	of	energy	related	information.		
From	 the	 narratives	 that	 were	 built	 during	 the	 FGs’	 roundtable	 discussion,	 one	 could	 expect	 that	 the	
provision	 of	 targeted	 information	 could	 encourage	 adoption	 of	 more	 energy	 efficient	 behaviours	 yet	
evidence	within	this	research	is	mixed,	with	FGs’	participants	being	divided.	Some	of	the	FGs’	participants	
agreed	that	if	they	knew	exactly	what	to	do,	they	would	act	in	accordance	and	others	reported	that	at	best	
they	would	know	they	are	doing	something	they	should	not,	but	would	not	change	existing	practices	and	
habits.	However,	FGs’	participants	seemed	to	be	more	receptive	to	personalized	information,	rather	than	
selecting	for	themselves	what	is	important	or	not.	For	this	reason,	a	face-to-face,	tailored,	information	type	
of	intervention,	such	as	an	energy	audit	might	still	be	an	effective	type	of	intervention,	to	at	least	impact	
the	 level	 of	 awareness,	 regarding	 more	 energy	 efficient	 behaviour.	 The	 impact	 this	 type	 of	 intervention	
would	have,	in	terms	of	generating	energy	savings,	needs	evaluation.	
8.3.2 	Information	and	communication	campaigns	
During	FGs,	participants	were	asked	to	recall	information	and	communication	campaigns	that	promoted	the	
adoption	 of	 more	 energy	 efficient	 behaviour,	 to	 discuss	 their	 efficacy	 as	 well	 as	 to	 suggest	 perceived	
requirements	that	could	lead	to	their	effectiveness.	FGs’	participants	recalled	six	energy	saving	campaigns,	
however,	considering	the	total	of	41	FG	participants,	this	could	be	interpreted	as	a	low	number.	During	the	
follow	up	discussion,	FGs’	participants	appeared	to	be	less	aware	of	energy	related	campaigns,	compared	to	
other	pro-environmental	fields	such	as	recycling.
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Most	 of	 FGs’	 participants	 provided	 a	 positive	 evaluation	 towards	 the	 role	 that	 communication	 and	
information	campaigns	can	play,	in	terms	of	providing	information	and	raising	the	awareness	about	more	
energy	 efficient	 behaviour.	 	 However,	 they	 were	 less	 certain	 of	 how	 effective	 these	 campaigns	 were	 in	
persuading	people	to	adopt	more	energy	efficient	behaviour.	Most	of	the	FGs’	participants	reported	to	be	
unsure	if	information	and	communication	campaigns	could	lead	them,	or	the	others,	to	adopt	more	energy	
efficient	behaviour:	
“Woman(W)1:	 Campaigns	 are	 useful	 but	 insufficient,	 (to	 promote	 behavioural	 change),	
…W1:	and	they	won’t	manage	to	reach	everybody…W2,	(complementing	the	idea	from	W1):	
people	hold	strong	ideas,	I	always	did	things	this	way	why	should	I	change	now,	(discussing	
the	adoption	of	more	energy	efficient	behaviours)”	FG7	
“W1:	 we	 see	 a	 campaign	 providing	 information	 on	 how	 we	 could	 save…W2	 it’s	 only	 an	
advertisement…W3:	 we	 don’t	 pay	 much	 attention…W1:	 one	 reads	 but	 doesn’t	
memorize…W2:	we	do	nothing,	unless	we	are	touched	for	some	reason	like	the	recycling	
campaigns	or	those	campaigns	to	feed	people	in	need…those	messages	have	an	impact”	
FG6	
Findings	thus	indicate	that	information	and	communication	campaigns	could	be	effective	in	encouraging	
the	adoption	of	more	energy	efficient	behaviour,	but	that	this	encouragement	alone	might	not	be	sufficient	
due	to	a	basic	lack	of	motivation	to	adopt	more	energy	efficient	behaviour.		
During	the	FGs,	participants	were	asked	to	design	an	information	and	communication	campaign	that	could	
be	 implemented	 nationwide	 in	 order	 to	 promote	 the	 adoption	 of	 more	 energy	 efficient	 behaviour.	 The	
issues	discussed	during	the	design	process	were	wide	ranging	and	highlighted	the	complexity	of	promoting	
the	 adoption	 of	 more	 energy	 efficient	 behaviour,	 with	 a	 number	 of	 desirable	 characteristics	 of	 future	
communication	and	information	campaigns	emerging.	Among	these,	FGs’	participants	focused	on	the	need	
to	provide	information	regarding	the	contribution	for	specific	individual	home	appliances	and	associated	
practices,	 as	 well	 as	 how	 much	 could	 be	 saved	 by	 adoption	 different	 behaviours.	 This	 shows	 that	 FGs’	
participants	 attributed	 a	 high	 level	 of	 relevance	 to	 understanding	 how	 much	 energy	 specific	 home
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appliances	consume	and	how	energy	is	used	within	day-to-day	practices,	in	order	to	consider	to	adopt	more	
energy	efficient	ones.	This	is	well	in	line	with	the	discussion	in	section	8.4.1	and	provides	further	evidence	
that	 FGs’	 participants	 and	 CID	 interviewees	 lack	 information	 regarding	 energy	 used	 under	 specific	
circumstances	and	as	a	consequence,	of	how	much	energy	could	be	saved.	Also,	FGs’	participants	focused	
on	 providing	 positive	 messages	 that	 could	 enhance	 the	 ‘fun’	 part	 of	 saving	 energy,	 rather	 than	 on	 the	
perceived	obligation	of	doing	so.	
“To	have	a	ghost	that	went	behind	and	switched	lights	off”	Female,	FG7	
“I	don’t	think	there	is	the	need	for	recrimination…I	believe	that	to	recriminate	introduces	a	
negative	 dimension	 that	 I	 don’t	 find	 essential	 for	 changing	 behaviours…the	 child	 can	
suggest	 to	 the	 mother	 and	 the	 mother	 can	 answer	 that	 you	 are	 right,	 I	 was	 not	 even	
recognizing	 what	 I	 was	 doing,	 (discussion	 during	 the	 design	 of	 the	 communication	
campaign),	Female,	FG2	
Positive	messages	were	perceived	as	stressing	the	results	of	saving	behaviour,	which	might	be	a	reason	for	
all	 suggested	 campaigns	 to	 have	 very	 similar	 slogans,	 focusing	 on	 the	 idea	 of	 saving,	 on	 short	 term-
immediate	change,	and	highlighting	the	financial	impact	of	saving.	These	findings	highlight	FGs’	participants	
focus	 on	 short-term,	 immediate	 gains	 rather	 than	 long-term	 investments	 in	 energy	 efficiency,	 which,	 in	
general,	is	opposite	to	the	majority	of	campaigns	that	focus	on	long-term	gains,	as	well	as	more	abstract	
terms	of	saving	the	environment,	or	saving	the	planet.	A	more	recent	communication	campaign	in	Portugal	
has	 been	 stressing	 the	 immediate	 gain,	 in	 particular	 the	 cost-saving	 potential	 day-to-day,	 that	 energy	
efficient	 behaviour	 can	 have.	 Only	 a	 few	 FGs’	 participants	 agreed	 to	 the	 use	 of	 shock,	 fear,	 or	 blame	
messages	to	promote	more	energy	efficient	lifestyles.	These	messages	were,	for	the	majority	of	the	FGs’	
participants,	perceived	as	not	contributing	to	the	success	of	the	campaign	and	FGs’	participants	used	the	
example	of	cigarette	packets	with	warning	messages	and	images	and	how	smokers	found	a	way	to	avoid	
these	by	buying	a	cover	for	the	packet.	Analogous	to	positive,	fun	messaging,	the	opposite,	fear	and	blame	
messaging,	 were	 perceived	 as	 not	 leading	 to	 individual	 identification,	 as	 there	 seemed	 to	 be	 a	 related	
fatigue	 and	 tiredness	 regarding	 negative	 messages	 that	 could	 enhance	 a	 feeling	 of	 helplessness	 and	
guiltiness	and	as	a	consequence,	of	disempowerment:
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“Nowadays	we	are	addressed	each	day	with	negative	things…it’s	too	much”	Female,	FG7	
“I	 would	 become	 very	 frustrated	 since	 I	 already	 save	 in	 so	 many	 things,	 with	 more	 energy	
efficient	light	bulbs	and	whatsoever,	that	I	believe	I	have	the	right	of	having	a	longer	shower”	
Female,	FG6	
Overall,	findings	from	the	FGs	suggest	that	communication	and	information	campaigns	can	be	used	as	a	
way	 to	 provide	 information	 and	 to	 generally	 highlight	 the	 benefits	 of	 adopting	 more	 energy	 efficient	
behaviour.	Findings	indicate	further,	that	information	campaigns	might	not	necessarily	lead	to	action	since	
there	might	be	a	lack	of	motivation	to	adopting	more	energy	efficient	behaviour.	As	such,	findings	from	this	
research	do	support	the	literature	in	that	communication	and	information	campaigns	might	have	little,	or	
no,	 impact	 on	 promoting	 individual	 behavioural	 change	 and	 thus	 can	 be	 expensive	 in	 relation	 to	 their	
effectiveness,	(Southerton	et	al.,	2011;	McKenzie-Mohr	2000).	
8.3.3 	Education	interventions	
During	 the	 FGs,	 the	 provision	 of	 formal	 education	 emerged	 as	 one	 of	 the	 interventions	 that	 could	
encourage	the	adoption	of	more	energy	efficient	behaviour	by	current,	as	well	as	 future	generations.	A	
number	of	FGs’	participants	acknowledged	that	during	their	school	education	there	were	not	that	many	
educative	 programmes	 that	 provided	 them	 with	 an	 understanding	 of	 the	 environmental	 impact	 of	 their	
behaviour.	
“My	son	went	to	the	kindergarten	and	teachers	focus	a	lot	on	the	environment,	not	on	the	use	
of	water	or	electricity	but	rather	in	terms	of	recycling	and	the	environment”	Female,	FG6	
However,	they	noticed	that	nowadays,	children	at	school	learn	how	to	behave	in	a	more	environmentally	
friendly	way,	providing	the	example	of	recycling	as	one	such	intervention	area.	As	a	result	of	this	school	
effort,	 FGs’	 participants	 agreed	 overall	 that	 this	 could	 have	 a	 positive	 impact	 on	 their	 children’s	 future	
behaviour,	which	potentially	could	be	more	energy	efficient	and	environmental	friendly	and	simultaneously	
have	 a	 side	 effect	 on	 the	 parents’	 behaviours	 as	 a	 result	 of	 child	 influence	 and	 pressure.	 Yet,	
simultaneously,	 this	 is	 also	 an	 example	 of	 how	 FGs’	 participants	 do	 not	 perceive	 themselves	 as	 being
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responsible	 for	 their	 current	 behaviour	 in	 terms	 of	 energy	 use	 at	 home.	 During	 the	 FGs,	 a	 number	 of	
participants	 referred	 to	 the	 pressure	 they	 felt	 from	 their	 children	 to	 recycle	 at	 home	 and	 how	 this	 has	
become	ingrained	into	the	family	routine.	Yet,	in	the	case	of	energy,	such	pressure	could	not	be	clearly	
identified.	Nevertheless,	this	might	also	be	related	to	the	fact	that	recycling	education	efforts	have	a	long	
tradition	within	the	Portuguese	school	system,	as	opposed	to	the	energy-focused	interventions	that	are	
more	recent.		
8.3.4 	Community	based	interventions	
Findings	from	this	research	suggest	FGs’	participants	and	CID/PID	interviewees	value	their	ability	to	provide	
their	families	with	comfort	and	wellbeing	levels	that	are,	socially,	perceived	as	required	and	desirable	to	
have,	regardless	of	the	amount	of	energy	that	is	required	to	supply	these.	During	the	FGs	and	CID/PIDs,	
participants	 and	 interviewees	 often	 compared	 their	 energy	 use	 to	 those	 of	 family	 members,	 friends,	 or	
people	having	a	house	with	similar	characteristics.	This	was	perceived	as	sufficient	to	justify	their	energy	
use	at	home	as	normal,	or	average,	even	if	it	included	non-essential,	but	rather	desirable	needs.	Shared	
practices	that	are	perceived	as	part	of	this	normal	energy	use	include	owing	several	TV	sets,	having	more	
than	one	shower	per	day,	or	leaving	home	appliances	on	stand-by	mode;	with	the	first	two	representing	a	
normal	comfort	level	and	the	last	the	convenience	of	less	energy	efficient	behaviour.	The	understanding	of	
normal	energy	use	as	a	comparison	has	been	discussed	in	chapters	6	and	7	and	further	explored	within	a	
reward-penalty	system	in	section	8.2.1.	By	calculating	the	base	energy	use	level,	household	energy	use	can	
be	 compared	 against	 other	 households	 and	 would	 allow	 identification	 of	 those	 households	 that	 have	
average	consumption	and	those	that	over-consume	or	under-consume	energy	at	home.	Nevertheless,	only	
one	of	the	PID	interviewees,	(PID3),	was	in	favour	of	such	an	approach	since	it	was	considered	to	appeal	to	
a	competitive	nature	and	would	influence,	what	he	understood	as	an,	individual’s	unwillingness	to	lose	at	a	
game.	
“I	guess	those	examples	you	provided,	to	measure,	to	use	inexpensive	monitoring	equipment	
to	reach	the	consumer,	to	guide	the	consumer	in	real	time.	The	truth	is	not	for	those	in	energy	
poverty,	but	for	the	others	this	is	small	money	when	compared	to	a	restaurant	bill	or	a	cinema
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ticket.	 People	 will	 save	 more	 by	 enrolling	 in	 a	 game,	 that	 will	 stimulate	 their	 competitive	
behavior,	no	one	likes	to	lose	a	game”,	PID3	
Ultimately,	it	appeard	as	if	the	relative	and	comparative	aspect	of	energy	use	did	support	building	up	an	
understanding	of	what	is	understood	as	being	a	normal	consumption,	which	in	the	case	of	relative	over-
spending	would	thus	be	a	questionable	incentive	to	use	less	energy,	in	combination	with	feedback	provision	
and	 monitoring	 equipment,	 (see	 8.4.3).	 Nevertheless,	 the	 results	 from	 this	 research	 are	 not	 conclusive	
regarding	 the	 effectiveness	 of	 how	 such	 a	 comparison	 system	 would	 encourage	 the	 adoption	 of	 more	
energy	efficient	behaviour.	But,	to	provide	feedback	on	energy	use,	based	on	a	comparison	system,	could	
be	 an	 alternative	 to	 complement	 the	 provision	 of	 individual	 feedback	 regarding	 energy	 use	 and	
improvement	 in	 the	 effectiveness	 of	 interventions.	 	 As	 such,	 collective	 feedback	 strategies	 that	 use	
neighbourhood	 data	 to	 feed	 comparitive	 use	 data,	 may	 be	 a	 useful	 addition	 to	 individual	 household	
feedback	as	an	intervention	strategy,	that	encourages	the	adoption	of	more	energy	efficicent	behaviours.	
8.4 	Combined	structural/psychological	interventions			
This	 section	 provides	 an	 overview	 on	 aspects	 that	 have	 been	 discussed	 within	 the	 FGs	 from	 both,	 a	
structural	and	psychological	intervention	perspective	that	are,	thus,	presented	in	this	section,	providing	a	
combined	look	at	structural	and	psychological	intervention.		
8.4.1 Information,	feedback	and	monitoring	equipment	
There	 was	 an	 overall	 agreement	 among	 FGs’	 participants	 and	 PID	 interviewees	 regarding	 the	 role	 that	
monitoring	equipment	could	have	as	a	way	of,	“Commoditizing”,	behaviour	into	a	good	proxy,	in	order	to	
make	consumption	visible,	as	suggested	by	WWF	(2008).	FGs’	participants	and	PID	interviewees	suggested	
the	 use	 of	 monitoring	 systems,	 such	 as	 energy	 meters,	 as	 one	 suitable	 option	 of	 providing	 continuous	
feedback	about	the	amount	of	energy	being	used.	During	PID,	interviewees	acknowledged	the	difficulty	that	
energy	invisibility	could	add	to	the	aim	of	promoting	the	adoption	of	more	energy	efficient	behaviour,	as	
well	as	the	role	that	monitoring	equipment	could	have	in	terms	of	providing	some	visibility	to	home	energy	
use,	as	the	following	quote	demonstrates:
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“One	of	the	most	important	aspects	for	changing	energy	use	is	its	visibility.	During	the	
'ecofamílias'
17
	 project	 with	 the	 use	 of	 energy	 meters…we	 managed	 to	 materialize	
energy,	something	that	otherwise	is	invisible	and	we	did	it	fairly	successfully”,	PID1	
Though	only	a	few	FGs’	participants	had	experience	with	energy	meters,	the	majority	of	FGs’	participants	
agreed	that	in	order	to	be	effective,	such	type	of	monitoring	equipment	must	provide	simple	information.	
During	the	FGs	some	examples	of	what	was	meant	by	simple	information	were	provided,	such	as	a	simple	
colour	system	indicating	whether	consumption	was	within	a	certain	range,	or	simple	alerts	triggered	once	
reaching	a	defined	value,	with	the	information	supplied	in	Euros	and	other	units,	such	as	kW	or	CO2,	an	add-
on	that	could	be	provided	if	wanted.	This	same	opinion	was	shared	among	PID	interviewees,	who	agreed	
that	provided	information	should	be	simple,	in	order	to	be	useful	and	support	individual	decision-making.	If	
these	conditions	were	met,	energy	meters,	or	similar	monitoring	equipment,	were	perceived	as	holding	a	
potential	 to	 promote	 more	 energy	 efficient	 behaviour	 and	 thus	 for	 energy	 to	 be	 saved.	 However,	 this	
almost	unanimous,	opinion	regarding	the	use	of	energy	meters,	or	similar	monitoring	equipment,	might	
need	 to	 be	 evaluated	 with	 care,	 since	 when	 questioned	 about	 the	 effectiveness	 of	 providing	 real	 time	
information	 and	 how	 this	 could	 influence	 the	 adoption	 of	 more	 energy	 efficient	 behaviours,	 three	
alternative	opinions	emerged	among	FGs’	participants:	(1),	those	FGs’	participants	that	were	convinced	of	
the	 benefits	 of	 knowing	 their	 detailed	 energy	 use,	 as	 this	 would	 lead	 to	 the	 adoption	 of	 more	 energy	
efficient	behaviours;	(2),	those	that	recognized	that	holding	this	level	of	feedback	would	be	of	interest	to	
them,	though	it	would	not	have	an	impact	in	terms	of	the	adoption	of	more	energy	efficient	behaviours;	
and	 (3),	 those	 that	 were	 not	 interested	 at	 all	 in	 learning	 about	 their	 energy	 use,	 since	 this	 could	 cause	
feelings	of	frustration	and	disappointment:	
“But	it	is	only	a	soup	I’m	warming	up”	(note:	when	discussing	the	impact	of	knowing	how	
much	 energy	 was	 spent	 for	 warming	 up	 a	 soup	 at	 the	 microwave	 and	 whether	 this	 could	
influence	 her	 individual	 behaviour,	 which	 was	 perceived	 as	 severely	 conditioned	 by	 her	
financial	situation	already),	Female,	FG7	
																																																																				
17
	Ecofamílias	project	had	3	editions	and	involved	a	total	of	1.225	families	with	the	aim	of	evaluating	their	ability	to	reduce	their	energy	
use	at	home.
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This	 diversity	 of	 opinion	 thus	 questions	 the	 effectiveness	 of	 providing	 real	 time	 feedback;	 whether	
monitoring	equipment	could	promote	long-term	adoption	of	more	energy	efficient	behaviours,	or	whether	
this	would	rather	be	a	short-term	phenomenon.	Though	FGs’	participants	acknowledged	the	potential	of	
monitoring	systems	to	allow	them	to	improve	their	knowledge	regarding	the	contribution	of	specific	energy	
related	 behaviours	 to	 their	 monthly	 bill,	 even	 those	 FGs’	 participants	 in	 favour	 of	 having	 a	 monitoring	
system	at	home	shared	the	opinion,	that,	with	time,	they	might	lose	interest	in	constantly	monitoring	their	
energy	use.	For	this	reason	monitoring	equipment	might	only	have	a	short-medium	term	impact:	
“I	have	no	idea	how	the	monitoring	equipment	would	be	but	if	I	would	need	to	check	for	the	
energy	being	used	each	time,	I	used	x	amount	of	energy,	I	used	x	amount	of	energy,	I	believe	I	
would	get	upset	after	a	while”,	Female,	FG7	
The	potential	effectiveness	of	the	use	of	monitoring	equipment	in	combination	with	prompting	strategies	
will	be	further	discussed	in	the	subsequent	section.	
8.4.2 	Smart	metering	and	prompting	strategies	
Prompting	 strategies	 appeared	 to	 be	 less	 known,	 though	 ultimately,	 FGs’	 participants	 provided	 several	
examples.	 One	 FGs’	 participant	 used	 post-it	 notes	 to	 remind	 family	 members	 on	 what	 they	 should	 do,	
another	one	referred	to	a	mobile	phone	that	produces	a	noise	once	charged,	or	another	referred	to	home	
appliances	that	produced	some	kind	of	sound	as	a	reminder	that	they	are	still	in	standby	mode.	Overall,	the	
inclusion	 of	 integrated	 smart	 features	 into	 home	 appliances	 appeared	 to	 be	 very	 well	 accepted	 by	 the	
majority	 of	 the	 FGs’	 participants,	 which	 could	 provide	 opportunities	 to	 effectively	 prompt	 individual	
behaviour,	with	the	message	being	displayed	in	close	proximity	to	the	place	where	the	target	behaviour	can	
be	performed,	as,	for	example,	suggested	by	Geller	et	al.,	(1982),	three	decades	ago.	These	smart	features	
were	perceived	by	FGs’	participants	as	having	a	prompting	role	in	reminding	users	to	adopt	more	energy	
efficient	behaviour	in	order	to	reduce	energy	use.	Findings,	thus,	suggest	that	prompting	strategies	could	be	
the	counterpart	to	the	barrier	of,	“I	forgot	doing	so”	and	fall	in	line	with	literature	claims	(see	section	4.5.1.)	
that	smart	features	hold	great	potential	due	to	their	proximity	to	where	the	action	takes	place.	Findings	
thus	support	earlier	studies	that	suggest	smart	features	could	be	a,	relatively,	low	cost	type	of	intervention,
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to	 promote	 the	 adoption	 of	 more	 energy	 efficient	 behaviours,	 (Lehman	 &	 Geller,	 2004).	 Yet,	 FGs’	
participants	felt	overall	that	these	prompts	should	be	stated	positively,	to	avoid	eliciting	negative	reactions,	
(see	also	8.3.2)	and	that	they	should	be	labelled	to	provide	information	designed	to	help	consumers	make	
informed	choices,	(see	also	8.2.3).	
8.4.3 	Information,	feedback	and	energy	bills	
According	to	the	findings	in	this	research,	energy	bills	might	not	be	the	most	efficient	strategy	to	provide	
people	with	information	on	how	much	energy	they	have	used,	or	at	least	not	for	the	case	of	Portugal.	The	
majority	of	FGs’	participants	found	it	difficult	to	understand	how	much	energy	they	used	during	a	specific	
month	for	a	number	of	reasons:	in	Portugal	energy	bills	include	other	fees	and	surcharges	not	related	to	the	
amount	of	energy	being	consumed,	often	they	are	bi-monthly,	(each	covering	two	months)	and	based	on	an	
estimated	 annual	 consumption,	 or	 fixed	 for	 11	 months.	 As	 a	 result	 of	 this,	 FGs’	 participants	 reported	
difficulty	in	understanding	the	amount	of	energy	used	for	a	specific	month,	as	well	as	what	might	have	
contributed	to	a	differing	energy	use	per	month.	Only	a	few	FGs’	participants	appeared	to	be	well	informed	
about	their	actual	monthly	energy	use	and	were	quite	happy	and	willing	to	share	the	data.	FGs’	participants	
suggested	that	in	order	to	be	more	useful,	energy	bills	should	provide	information	in	an	easily	understood	
way,	such	as	a	bar	graph	with	monthly	consumption	based	on	real	consumption,	or	a	comparison	in	a	way	
they	 could	 relate	 to,	 such	 a	 basic	 home	 appliance.	 Overall	 findings	 from	 FGs	 are	 well	 in-line	 with	 the	
literature,	(Brandon	&	Lewis,	1999;	Darby,	2006)	and	provide	further	evidence	on	the	role,	but	also	the	
limitations	for	energy	bills	to	provide	useful	feedback	on	energy	use.		
8.5 	Concluding	remarks	
This	chapter	discusses	the	findings	from	the	empirical	study	looking	at	the	potential	effectiveness	different	
intervention	strategies	to	encourage	the	adoption	of	more	energy	efficient	behaviours	at	home	within	the	
Portuguese	context.
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In	 the	 following	 table	 the	 findings	 from	 the	 research	 presented	 in	 this	 chapter	 are	 related	 to	 RQ3,	
highlighting	including	any	noteworthy	deviation	from	the	reviewed	literature	that	could	be	detected	from	
the	findings	of	this	research	
.
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Empirical	study	findings	 RQ	 Noteworthy	further	observations	
	Chapter	Section:	8.1.	Communication	Design	
Persuading	people	to	adopt	more	energy	efficient	behaviour,	
generally	seen	as	challenging	for	less,	‘easy	and	simple’,	
behavioural	changes,	or	once	not	having	an	impact	on	desired	
normal	levels	of	comfort,	convenience	or	wellbeing.	
RQ3b	 		
People	 do	 not	 appear	 to	 hold	 any	 inconsistency	 between	 their	
attitudes	and	their	behaviour,	if	one	considers	that	their	positive	
attitudes	towards	comfort	and	wellbeing	are	stronger	than	their	
attitude	towards	the	environment.	
RQ3a	 		
Previous	 messages	 from	 interventions	 do	 not	 appear	 to	 be	
aligned	 with	 those	 behaviours	 that	 people	 accept	 doing,	 but	
rather	to	the	ones	they	reject,	or	are	not	committed	to	doing.	
RQ3a	
		
	Chapter	Section:	8.2.	Structural	interventions	
8.2.1.	Rewards	and	punishments	
Findings	 suggest	 that	 a	 rewards/punishment	 system	 might	 be	
effective	 for	 some	 people	 to	 encourage	 the	 adoption	 of	 more	
energy	efficient	behaviour.	
RQ3a,	RQ3b	
The	potential	effectiveness	of	rewards/punishment	system	could	not	be	fully	understood,	in	
particular	to	the	medium/long	term.	
8.2.2.	Provision	of	incentives	and	samples	
Findings	 suggest	 the	 provision	 of	 incentives	 and	 samples	 could	
encourage	the	introduction	of	more	energy	efficient	technologies	
by	reducing	the	investment	required	and	risk	of	such	a	purchase.	
RQ3a
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Empirical	study	findings	 RQ	 Noteworthy	further	observations	
8.2.3.	Labelling	
The	efficacy	of	labelling	could	not	be	fully	understood,	as	people	
might	 lack	 the	 ability	 to	 fully	 understand	 the	 information	
provided.	
RQ3b	
‘A	rated’	seen	as	synonym	for	energy	efficient,	without	considering	actual	use.	
Observed	lack	of	ability	across	all	FGs	to	understand	energy	labels,	to	use	them	as	a	means	to	
actually	compare	the	performance	of	home	appliances,	resulting	in	an	apparent	lack	of	
effectiveness	of	such	labels.	
8.2.4.	Demonstrating	and	facilitating	as	an	intervention	strategy	
Modelling	behaviour	was	seen	as	a	potentially	effective	avenue	
for	 changing	 behaviour,	 as	 people	 will	 follow	 these	 examples	
once	 they	 are	 understandable,	 relevant,	 meaningful	 and	
rewarding,	in	terms	of	positive	results.	
RQ3a,	RQ3b	
		
8.2.5.	Environmental	design	and	material	contextual	adjustment	
Even	 though	 the	 contribution	 of	 technology	 could	 play	 an	
important	 role,	 there	 is	 some	 common	 agreement	 that	
technological	 solutions	 to	 domestic	 energy	 reduction	 might	 be	
insufficient	without	the	cooperation	of	individuals.	
RQ3a	
Apparent	neglecting	of	interventions	aimed	at	how	the	home	and	home	appliances	are	used	
and	how	they	can	be	adjusted	on	an	everyday	base.	
Product	design	and	contextual	adjustments	could	be	effective,	but	will	not	necessarily	
encourage	the	adoption	of	more	energy	efficient	behaviour,	being	a	more	technofix	approach.
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Empirical	study	findings	 RQ	 Noteworthy	further	observations	
Chapter	Section:	8.3.	Psychological	interventions	
8.3.1.	Targeted	face-to-face	information	and	feedback	
Face-to-face	information	appears	to	be	the	desirable	alternative	
to	received	customized	information,	yet	it	might	not	lead	to	the	
adoption	of	more	energy	efficient	behaviour.	
RQ3a	
Information	should	be	provided	first	in	monetary	terms,	and	potentially	also	in	other	units	such	
as	CO2.	
Overall	concern	regarding	which	information	is	correct	and	whom	can	people	trust.		
8.3.2.	Information	and	communication	campaigns	
Information	and	communication	campaigns	are	perceived	as	an	
adequate	 alternative	 to	 provide	 information	 and	 raising	
awareness,	 but	 might	 have	 little	 or	 no	 impact	 on	 encouraging	
behavioural	change.	
RQ3a,	RQ3b	
Low	incidence	of	recall	for	energy	saving	campaigns	
Encouragement	 via	 information	 and	 communication	 alone	 might	 not	 be	 sufficient	 to	 lead	 to	
change	due	to	a	basic	lack	of	motivation	to	adopt	more	energy	efficient	behaviour.	
FGs’	 participants	 focused	 on	 providing	 positive	 messages	 that	 could	 enhance	 the	 fun	 part	 of	
saving	energy	rather	than	on	the	perceive	obligation	of	doing	so.	
8.3.3.	Education	interventions	
The	provision	of	education	is	perceived	as	an	effective	strategy	to	
encourage	 the	 adoption	 of	 more	 energy	 efficient	 behaviour	 by	
todays’	and	future	generation.	
RQ3a,	RQ3b	
Recycling	as	an	example	for	perceived	success	of	behavioural	change	interventions	in	Portugal.	
Recycling	as	an	example	for	children	pressuring	parents	to	recycle	at	home	and	how	this	
became	ingrained	into	the	family	routine.	
8.3.4.	Community	based	interventions	
Comparing	 individual	 energy	 use	 to	 that	 of	 other	 community	
members	could	be	an	effective	means	of	information	provision,	
that	could	provoke	and	encourage	the	adoption	of	more	energy	
efficient	behaviour	by	providing	comparative	feedback,	a	feeling	
of	competition,	social	comparison,	or	social	pressure.	
RQ3a,	RQ3b	
Collective	feedback	strategies	that	use	neighbourhood	data	to	feed	comparative	use	data,	may	
be	a	useful	addition	to	individual	household	feedback	as	interventions	that	encourage	a	change	
in	energy	behaviour.
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Empirical	study	findings	 RQ	 Noteworthy	further	observations	
Chapter	Section:	8.4.	Structural/Psychological	interventions	
8.4.1.	Information,	feedback	and	monitoring	equipment	
Information	 should	 be	 provided	 firstly	 in	 monetary	 terms,	 and	
potentially	also	in	other	units,	such	as	CO2.	
RQ3a	
The	use	of	energy	meters,	in	terms	of	acceptance	and	impact	level,	apparently	do	vary,	ranging	
between	appreciation	to	annoyance.	
8.4.2.	Smart	metering	and	prompting	strategies	
Prompts	could	be	an	effective	intervention	to	remember	easy	to	
do	activities.	
RQ3a	
FGs’	participants	overall	felt	these	prompts	should	be	stated	politely	to	avoid	eliciting	negative	
reactions,	(see	also	8.3.2)	and	that	they	should	be	labelled	in	such	a	way	as	to	provide	
information	designed	to	help	consumers	make	informed	choices,	(see	also	8.2.3).	
Smart	 features	 could	 be	 a,	 relatively,	 low	 cost	 type	 of	
intervention	 to	 promote	 the	 adoption	 of	 more	 energy	 efficient	
behaviour.		
RQ3a	
Integrated	smart	features	could	provide	a	set	of	opportunities	to	effectively	prompt	individual	
behaviour,	with	the	message	being	displayed	in	close	proximity	to	the	place	where	the	target	
behaviour	can	be	performed.	
8.4.3.	Information,	feedback	and	energy	bills	
		 RQ3b	
Energy	bills	might	not	be	the	most	efficient	strategy	to	provide	people	with	information	on	how	
much	energy	they	have	used.	
	
Table	8-1	–	Summary	of	findings	relating	to	RQ3
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Here,	a	summary	is	provided	on	how	the	results	reported	in	this	chapter	provide	answers	towards	research	
questions	3,	(RQ3),	“What	is	the	potential	role	of	intervention	strategies	on	energy	use	at	home”	and	the	
sub-questions,	 	 “What	 are	 perceived	 requirements	 of	 intervention	 strategies”,	 (RQ3a)	 and	 “What	 are	
individual	perceptions	on	the	effectiveness	of	intervention	strategies”,	(RQ3b).		
With	regards	to	the	perceived	requirements	of	intervention	strategies,	findings	presented	in	section	8.1	
highlight	how	important	it	is	to	send	the	appropriate	message	by	the	appropriate	messenger,	so	that	the	
target	audience	identifies	with	the	message	and	increases	the	likelihood	of	them	acting	as	desired.	As	can	
be	seen	across	sections	8.1	to	8.4,	persuading	people	to	adopt	more	energy	efficient	behaviour	appears	to	
be	 challenging	 and,	 in	 particular,	 for	 less	 ‘easy	 and	 simple’	 behavioural	 changes,	 or	 those	 perceived	 as	
impacting	desired	‘normal’	levels	of	comfort,	or	wellbeing.	As	shown	through	the	chapter	the	provision	of	
information	 and	 feedback,	 in	 its	 various	 forms,	 had	 been	 perceived	 as	 being	 efficient	 in	 providing	
information	and	raising	awareness	towards	more	energy	efficient	behaviour.	Yet,	once	it	came	to	individual	
experience	 and	 actions,	 it	 equally	 could	 be	 seen	 that	 FGs’	 participants	 did	 often	 appear	 to	 lack	 of	
motivation.	 In	 this	 regard	 it	 was	 not	 possible	 to	 understand	 how	 these	 perceived	 requirements,	 for	
interventions	to	be	successful,	could	address	the	observed	lack	of	motivation	for	adopting	more	energy	
efficient	behaviour,	and	that	they	frequently	appeared	to	be	anchored	on	the	motivation	to	provide	their	
family	 with	 socially	 agreed	 normal	 levels	 of	 comfort	 and	 wellbeing.	 With	 this,	 the	 overall	 efficacy	 of	
interventions	might	be	questioned.	These	findings,	do	however,	support	earlier	findings	that	information	
and	feedback	provision	alone	might	not	be	sufficient	to	effectively	encourage	the	adoption	of	more	energy	
efficient	 behaviour	 and	 thus	 might	 require	 information	 and	 feedback	 provisioning	 to	 be	 used,	 in	
combination	 with	 other	 type	 of	 interventions,	 so	 to	 increase	 their	 chance	 of	 success,	 as	 suggested,	 for	
example,	by	Abrahamse	et	al.	(2005),	or	Southerton	et	al.	(2011).	During	the	empirical	study,	an	example	of	
such	 a	 combination	 emerged	 and	 was	 related	 to	 the	 need	 for	 information	 and	 feedback	 to	 be	 used	 in	
combination	 with	 promoting	 the	 adoption	 of	 a	 social	 understanding	 of	 normal	 energy	 use.	 As	 such	
information	 provision	 might	 not	 be	 a	 panacea	 for	 the	 effective	 adoption	 of	 more	 energy	 efficient	
behaviours.	As	could	be	seen	through	chapter	eight,	contextual	intervention	strategies	that	were	perceived	
as	 more	 efficient	 included,	 the	 adjustments	 within	 product	 design,	 house	 infrastructures	 and	 home	
appliances	and	all,	to	a	certain	degree,	removed	the	responsibility	from	the	user	to	adopt	more	energy
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efficient	 behaviour,(Southerton	 et	 al.,	 2011).	 An	 additional	 focus,	 thus	 might	 be	 placed	 on	 providing	
effective	incentives	and	punishments,	in	combination	with	a	community	level	type	of	intervention	drawn	on	
comparative	 feedback,	 instead	 of	 the	 individual	 approach	 that	 appears	 to	 have	 dominated	 so	 far,	 as	
suggested	by	Abrahamse	et	al.	(2005),	Darby	(2006),	EEA	(2013),	Heiskanen	et	al.	(2009),	or	Middlemiss	
(2008).
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196	
9 	Conclusion	
This	study	investigated	domestic	energy	use	behaviours	in	the	Portuguese	context	and	aimed	to	explore	
how	the	adoption	of	more	energy	efficient	behaviours	at	home	could	be	encouraged.	With	this	the	research	
has	three	objectives.	First	it	attempts	to	provide	an	overview	of	what	explains	and	influences	energy	use	at	
home	(RQ1).	Second	it	has	the	objective	to	advance	on	the	theory	of	motivating,	enabling	and	reinforcing	
factors	that	could	promote	the	adoption	of	more	energy	efficient	habitual	behaviours	and	practices	at	a	
household	 level	 (RQ2).	 Thirdly,	 this	 research	 has	 the	 objective	 to	 explore	 the	 potential	 effectiveness	 of	
change	interventions	within	the	field	of	energy	use	at	home	and	the	different	types	of	interventions	that	
might	be	used	(RQ3).	
9.1 Specific	answers	to	the	research	questions	
9.1.1 	RQ1:	What	explains	energy	use	at	home?	
As	has	been	shown	throughout	the	research,	energy	use	is	not	the	result	of	a	single	determinant,	but	rather	
the	result	from	a	number	of	internal	and	external	determinants.	The	determinants	and	existing	conditions	
found	through	this	research,	appear	to	be	in	overall	support	of	the	literature	presented	in	chapter	2	and,	
notably,	with	the	works	of	BPIE	(2011),	DGGE/IP-3E	(2004),	Goldblatt	(2005)	and	Maréchal	(2010).	With	
regards	to	home	appliances,	this	research	provides	further	evidence	that	the	ever-increasing	number	of	
home	 appliances	 does	 increase	 energy	 use,	 (6.2.1;	 6.2.3).	 But,	 this	 simultaneously	 helps	 to	 trigger	
participants’	awareness	of	the	need	to	purchase	more	energy	efficient	appliances	so	to	reduce	energy	use,	
(6.2.4).	As	could	be	seen	in	both,	the	empirical	work	and	the	literature,	participants	not	only	substituted	
old,	obsolete	home	appliances,	but	also	bought	more	appliances	overall	(2.2.).	
Throughout	this	research,	the	availability	of	energy	was	never	truly	questioned	by	the	participants,	with	
energy	being	perceived	as	something	essential	for	people	to	live	in	the	way	we,	in	an	industrialised	nation’s	
context,	 have	 become	 used	 to,	 (6.1.2).	 With	 this,	 it	 could	 also	 be	 seen	 that	 energy	 is	 an	 intermediary	
between	need	and	fulfilment	of	need,	as	part	of	a	socio-economical-techno-cultural	combination	that	frame	
‘our’	needs,	opportunities,	belief	systems	and	abilities,	(7.1;	7.2.3).	Findings	from	the	empirical	study	did
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show	the	relation	between	‘energy	prices	&	energy	use’,	as	well	as	‘disposable	income	&	energy	use’,	with	
both	 constituting	 determinants	 for	 energy	 use,	 (6.2.4).	 Though	 saving	 money	 seemed	 not	 to	 be	 a	 main	
priority	for	the	adoption	of	more	energy	efficient	behaviour,	but	rather	to	maintain	existing	behaviour	as	
long	 as	 deemed	 affordable,	 (7.1.1).	 Findings	 from	 the	 FGs	 and	 interviews	 reveal	 a	 tendency	 for	 higher	
reported	income	levels	to	be	associated	with	higher,	reported,	energy	use,	with	participants	agreeing	that	
perceived	‘needs’	increase	with	income	level,	(6.2.5;	6.2.6.),	which	appeared	aspired	to	by	those	on	lower	
incomes,	(6.2.5.).	This	assumption	is	supported	by	earlier	research,	(WWF,	2012;	DECC,	2011;	Gatersleben	
et	al.,	2002;	2.2;	2.2.5.;	2.2.8).	Findings	from	this	research	indicate	that	the	majority	of	the	participants	will	
maintain	 their	 behaviour,	 even	 if	 prices	 increased,	 as	 long	 as	 they	 could	 afford	 doing	 so,	 (6.2.4),	 thus	
providing	further	evidence	to	the	body	of	literature	regarding	energy	use	as	price	inelastic	in	the	short	term,	
(DECC,	2011;	Gatersleben	et	al.,	2002,	Sorell,	2007;	2.2.4;	2.2.5;	2.2.8.).	However,	considering	that	overall	
energy	consumption	declined	in	Portugal	as	a	result	of	the	economic	crisis	(1.7)	this	also	suggests	that	some	
people	stopped	being	able	to	afford	their	former	energy	level.	More	precisely	it	could	be	observed,	(6.2.4;	
7.1.1),	that	energy	and	fuel	poverty	seem	to	be	a	reality	for	a	number	of	people	within	the	empirical	study,	
with	participants	not	being	able	to	guarantee	services	such	as	heating	their	homes,	or	to	afford	to	spend	
more	of	their	monthly	income	on	energy.	For	the	case	of	Portugal	it	also	could	be	seen	that	poor	building	
envelopes	and	infrastructures	(2.2.7)	could	further	impact	upon	energy	and	fuel	poverty.	In	any	of	such	
cases	 people	 are	 forced	 to	 use	 less	 energy	 if	 prices	 rise,	 which	 has	 also	 been	 found	 in	 other	 studies,	
(Boardman,	2010;	Buzar,	2007a;	Healy,	2003;	SEI,	2003;	SILC,	2007;	WHO,	2012;	2.2;	2.2.5.).	
This	research	further	shows	that	existing	habits	are	a	driving	force	for	energy	use	and	represent	a	challenge	
to	the	effective	adoption	of	more	energy	efficient	behaviour,	since	most	energy	related	behaviour	are	of	a	
habitual	 nature	 and	 often	 acquired	 over	 time,	 (7.3.1),	 supporting	 existing	 studies,	 (IPPR,	 2009;	 Green	
Alliance,	2011,	Jackson,	2005;	3.4.1).	
9.1.2 	RQ2:	What	influences	energy	use	at	home?	
As	 could	 be	 seen,	 barriers	 appear	 to	 influence	 energy	 use	 more	 than	 motivations	 and	 outnumbered	
motivations	in	each	of	the	three	phases	of	the	research;	even	existing	motivations	ultimately	did	not	appear	
to	result	in	any	actual	energy	usage	reduction,	(7.1;	7.2;	7.3).	Motivational	variables	appear	to	be	in	direct
9.	Conclusion	
	
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competition	with	barriers	and	findings	indicate	that	the	reported	barriers	are,	perhaps,	not	actual	barriers,	
but	in	part	a	convenient	excuse,	(7.3.4.).	Therefore,	energy	use	is	perhaps	less	influenced	by	‘being	able’	to	
adopt	 more	 energy	 efficient	 behaviour	 and	 more	 about	 ‘being	 willing’	 of	 doing	 so.	 As	 such,	 findings	 do	
support	the	literature	that	people	tend	to	say	that	they	cannot	perform	the	behaviour,	(low	self-efficacy),	
rather	than	they	will	not	perform	it	and,	in	particular,	once	they	anticipate	an	aversive	outcome,	such	as	
reduced	level	of	comfort,	they	are	no	longer	willing	to	adopt	behaviour	that	may	produce	such	an	outcome,	
(Allen	 and	 Ferrand	 1999;	 Baker	 &	 Kirsch,	 1991;	 Bandura,	 1986;	 DECC,	 2011;	 EEA,	 2013;	 Jackson,	 2005;	
Kollmuss	&	Agyeman,	2002;	Leiserowitz	et	al.,	2011a;	Prendergrast	et	al.,	2008;	Shove,	2003;	Vandenbergh	
et	al.,	2008;	3.4.2;	3.4.4).	This	could	help	explain	why	energy	use	has	not	been	decreasing	more	notably	in	
Portugal	 despite	 the	 growing	 number	 of	 governmental	 supported	 tangible	 and	 intangible	 interventions	
(1.7).		
This	is	also	supported	through	the	apparent	observed	importance	and	role,	of	norms,	habits	and	beliefs	
with	 regards	 to	 lack	 of	 efficacy,	 or	 the	 understanding	 of	 giving	 up	 something,	 that	 were	 frequently	
highlighted	as	main	barriers	towards	the	adoption	of	more	energy	efficient	behaviour	by	the	participants	of	
this	research,	(7.2.3;	7.3.1;	7.3.3).	Findings	further	reveal	that	attitudes	and	values	might	influence	energy	
use	at	home	once	it	comes	to	family	comfort	and	wellbeing,	with	values,	attitudes	and	behaviours	being	
well	aligned	and	resulting	in	a	potentially	higher	energy	use	at	home,	(7.1.2;	7.3.2;	8.1).	Furthermore,	there	
seemed	 to	 be	 an	 individual	 resistance	 towards	 specific	 behaviours	 that	 did	 compete	 with	 wellbeing,	
convenience	and	comfort,	(7.1.3;	7.3.2;	7.3.4),	as	has	also	been	found	in	other	studies,	(DECC,	2011;	EEA,	
2013;	Jackson,	2005;	Prendergrast	et	al.,	2008;	Shove,	2003;	2.2.2;	2.2.5;	3.3.1;	3.3.3;	3.4.2;	3.4.4).	
Participants	 appeared	 to	 be	 quite	 comfortable	 with	 a,	 certain,	 level	 of	 normal	 energy	 use	 and	 there	
appeared	to	be	a	socially	shared	understanding	of	this	normal	that	directly	seemed	to	influence	energy	use,	
(7.3.2),	as	is	also	known	from	the	literature,	(Goldblatt,	2005;	Maréchal,	2010;	Shove,	2004;	2.2.1;	2.2.3).	
Further	 to	 this,	 existing	 energy	 use	 habits	 were	 reported	 as	 highly	 influencing	 energy	 use,	 due	 to	 the	
difficulty	of	challenging	and	changing	such	habits	and	encouraging	more	energy	efficient	ones,	(7.3.1).	
In	 addition	 to	 this,	 findings	 from	 this	 research,	 (6.2.4;	 7.1.1;	 7.3.2),	 support	 the	 literature,	 (DECC,	 2011;	
Gatersleben	et	al.,	2002;	2.2;	2.2.5;	2.2.8),	that	a	higher	income	level	might	be	associated	to	higher	energy	
use.	Those	who	are	more	affluent	appear	willing	to	trade	money	for	what	they	see	as	normal	comfort	and
9.	Conclusion	
	
199	
convenience,	giving	priority	to	individual	and	family	wellbeing,	rather	than	for	environmental	protection.	
Nevertheless,	this	might	not	be	a	conscious,	“trade	off”,	between	energy	costs	in	relation	to	income,	but	
rather	that	energy	seems	to	be	cheap	to	some	of	the	participants	and	thus	there	is	no	rationale	to	consider	
reducing	 usage.	 A	 longer-term	 view,	 regarding	 environmental	 protection,	 might	 be	 required	 to	 build	 a	
response	to	this	sort	of	rational.	
In	contrast	to	this,	those	in	energy	and	fuel	poverty	appear	to	not	be	able	to	reach	the	aspired	normal	
comfort	level,	suggesting	that	an	increase	in	income	could	promote	higher	levels	of	energy	use	at	home,	
(6.2.5.).	This	research	provided	evidence	that	the	amount	of	those	in	fuel	poverty	might	be	higher	than	
what	is	commonly	perceived	and	much	in-line	with	the	existing	statistics	and	assumptions	from	literature,	
(Healy,	2003;	SEI,	2003;	SILC,	2007;	WHO,	2012).	
With	regards	to	these	factors	that	seem	not	to	influence	energy	use	at	home,	findings	from	this	research,	
(7.1.2;	8.1),	suggest	that	pro-environmental	values	and	attitudes	are	among	the	determinants	that	appear	
to	have	less	influence	on	the	amount	of	energy	being	used	at	home.	This	supports	the	findings	from	earlier	
studies,	(Kollmuss	&	Agyeman,	2002;	McKenzie-Mohr	&	Smith,	1999;	Poortinga	et	al.,	2004;	Schultz	et	al.,	
1995;	Thøgersen,	2004;	3.2).	
9.1.3 	RQ3:	What	is	the	potential	role	of	intervention	strategies	on	energy	use	at	home?	
Findings	 from	 this	 research	 suggest	 that	 any	 attempt	 to	 reduce	 energy	 use	 at	 home	 would	 face	 strong	
competition	 from	 the,	 perceived,	 normal	 level	 of	 use,	 (9.2.1).	 To	 support	 the	 adoption	 of	 more	 energy	
efficient	behaviour	at	home,	intervention	strategies	must	change	this	understanding	of	normal	to	a	clearly	
defined	new	level	that	is	considered	sustainable	and	desired,	(8.1).	During	this	research	it	was,	however,	
not	possible	to	understand	how	existing	norms	could	be	effectively	integrated	within	future	interventions,	
(6.2.5;	7.2.3;	8.2.1).	As	such,	little	evidence	was	uncovered	during	the	empirical	study	to	suggest	that	norms	
could	be	used	to	encourage	the	adoption	of	more	energy	efficient	behaviour,	(6.2.5),	as	suggested	by	the	
literature,	(section	2.2.3).	
Other	 strategies	 to	 interventions	 that	 might	 be	 adopted	 include	 choice	 architecture,	 product	 design,	 or	
penalty-incentive	 approaches,	 as	 they	 circumvent	 decision-making	 based	 on	 shared	 understandings	 of	
comfort,	 wellbeing	 and	 individual	 preference,	 (8.2.1;	 8.2.5).	 However,	 the	 literature	 suggests	 that	 such
9.	Conclusion	
	
200	
strategies	would,	in	addition,	need	to	pay	attention	to,	‘intrinsic	motivation’	and	cultural	and	infrastructural	
influences,	(Dwyer	et	al.,	1993;	Lutzenhiser,	1993;	Lowe,	1996;	Wilhite	and	Shove,	1998;	2.2.).	Since	a	focus	
on	‘knowledge-penalty-incentive-behaviour’	might	fail	to	recognise	the	complexity	and	dynamics	in	which	
energy	use	is	embedded	in	the	flow	of	day-to-day	life.	Thus,	the	ultimate	suitability	of	choice	architecture,	
product	design,	or	penalty-incentive	strategies,	perhaps,	would	need	to	be	further	examined	in	light	of	the	
existing	literature.	
Findings	 equally	 show	 that	 the	 evaluation	 of	 previous	 attempts	 might	 also	 impact	 the	 potential	
effectiveness	of	interventions.	Thus,	in	planning	intervention	strategies	it	might	be	required	to	consider	the	
outcome	expectations	people	have,	regarding	the	efficacy	of	individually	adopting	more	energy	efficient	
behaviour,	 as	 well	 as	 to	 collectively	 engage	 in	 them,	 (7.3.3;	 7.3.4).	 As	 has	 also	 been	 suggested	 in	 the	
literature,	(Bandura,	1977a;	Cialdini	et	al.,	1990;	Martiskainen,	2007;	van	der	Pligt,	1985;	3.3.3;	3.4.3).	
All	 of	 these	 findings	 also	 show	 that	 frameworks	 that	 attempt	 to	 support	 intervention	 strategies	 must	
provide	the	right	interplay	between	the	various	existing	factors	and	as	further	discussed	in	section	9.2.			
9.2 Key	findings	
This	section	provides	an	overview	of	the	key	results	of	this	research	and	the	contribution	it	makes	to	the	
field	of	knowledge	in	sustainable	energy	use.	A	particular	focus	is	on	how	the	adoption	of	more	energy	
efficient	behaviours	at	home	could	be	encouraged,	in	the	context	of	understanding	existing	determinants,	
motivating,	enabling	and	reinforcing	factors	and	the	related	implications	towards	intervention	strategies.	
The	findings	of	this	research	generally	show	that	if	the	rate	of	adoption	of	more	energy	efficient	behaviour	
is	 to	 increase,	 then	 interventions	 that	 are	 focusing	 on	 providing	 information	 or	 financial	 incentives	 are	
unlikely	 to	 work	 for	 a	 large	 proportion	 of	 energy	 users.	 Instead,	 the	 adoption	 of	 more	 energy	 efficient	
behaviour	 at	 home	 depends	 on	 the	 ability	 of	 intervention	 strategies	 to	 challenge	 existing	 norms,	 thus	
creating	 new	 understandings,	 expectations	 and	 utilization	 of	 energy	 services	 that	 could	 manifest	 in	 the	
adoption	of	more	energy	efficient	behaviour.	As	such	the	work	has	shown	that	community-based	initiatives	
might	 be	 an	 adequate	 means	 to	 challenge	 social	 norms	 and	 to	 bring	 about	 change	 and	 as	 detailed	 in	
following	sections.
9.	Conclusion	
	
201	
9.2.1 	Importance	to	challenge	the	understanding	of	normal	
Section	4.1	discussed	a	number	of	frameworks	that	could	support	intervention	strategies	and	that	attempt	
to	 provide	 the	 right	 interplay	 between	 the	 various	 existing	 factors.	 And	 indeed	 the	 findings	 from	 this	
research	do	support	the	impact	that	the	various	external,	internal	or	social	factors,	such	as	norms	or	habits,	
could	have.	With	this	findings	do	support	earlier	studies	that	(Prendergrast	et	al.,	2008)	informational	and	
financial	levers	alone	might	not	be	sufficient	to	promote	individual	behavioural	change,	but	instead	would	
require	frameworks	that	attempt	to	change	existing	perceptions,	knowledge,	attitudes,	norms	and	values	
(Abrahamse	et	al.,	2005),	or	that	go	beyond	the	individual	and	also	address	the	community	level	and	the	
social	aspects	of	energy-related	behaviour	(Abrahamse	et	al.,	2005;	Darby,	2006;	Heiskanen	et	al.,	2009;	
Middlemiss,	 2008).	 With	 this	 the	 findings	 of	 this	 research	 do	 suggest	 that	 the	 frameworks	 and	 models	
presented	in	sections	4.1	and	4.2	indeed	could	support	intervention	strategies	to	find	the	right	interplay.	A	
common	 finding	 across	 all	 of	 the	 three	 empirical	 phases	 of	 the	 research	 had	 been	 the	 unwillingness	 to	
adopt	 more	 energy	 efficient	 behaviour,	 mainly	 for	 the	 reason	 that	 they	 are	 perceived	 as	 impacting	
established	levels	of	comfort,	convenience	and	wellbeing,	(6.2.5;	7.3.2;	7.3.4).	This	unwillingness	appeared	
to	relate	to	what	is	perceived,	expected	and	socially	accepted	as	normal	energy	use,	normal	comfort	levels,	
normal	 services	 that	 energy	 provides,	 that	 have	 entered	 peoples’	 day-to-day	 lives,	 (7.1.3;	 7.3.2).	
Expectations	of	energy	services	and	use	are	normalised	in	terms	of	levels	of	comfort	and	to	challenge	that,	
in	 asking	 people	 to	 adopt	 different	 behaviour,	 challenges	 the	 core	 expectations	 that	 have	 become	
established,	(7.2.3;	8.1).		
From	such	a	perspective,	the	adoption	of	more	energy	efficient	behaviour	at	home	depends	on	the	ability	
of	intervention	strategies	to	challenge	the	existing	norm,	so	to	create	a	new	understanding	and	expectation	
of	energy	services	that	could	become	manifest	in	the	adoption	of	more	energy	efficient	behaviour,	(7.2.3;	
8.1).	As	can	further	be	seen,	the	ability	of	intervention	strategies	to	provide	opportunity	to	understand	and	
compare	 one’s	 energy	 use	 and	 to	 provide	 customized	 circles	 of	 information	 and	 feedback,	 (7.2.2;	 8.3.1;	
8.3.4;	 8.4.1;	 8.4.2),	 or,	 to	 question	 and	 promote	 debate,	 with	 regards	 to	 normal	 and	 taken-for-granted	
practices,	 (7.3.2),	 appear	 to	 hold	 high	 potential	 to	 increase	 the	 likelihood	 of	 success	 of	 intervention	
strategies.
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202	
9.2.2 	Invisibility	of	energy	and	its	implications	
Previous	research,	(Burgess	&	Nye,	2008;	Darby,	2006;	Hargreaves,	2012;	2.2.),	suggests	that	‘invisibility’	is	a	
distinctive	characteristic	of	energy	use	at	home	and	this	study	supports	this,	with	participants	considering	
energy	 as	 intangible	 and	 abstract	 when	 compared	 to	 other	 utilities,	 (6.1.1.).	 Participants	 compared	 the	
energy	 that	 flows	 in	 pipes	 inside	 the	 home	 to	 the	 water	 they	 see	 flowing	 out	 of	 the	 tap	 and	 energy	
invisibility,	indeed,	appeared	to	be	a	distinctive	characteristic	of	energy,	when	compared	to	other	utilities,	
(6.1.1.).	 Despite	 being	 a	 distinct	 characteristic,	 the	 empirical	 study	 did	 however	 equally	 provide	 some	
evidence,	(6.1.1.),	that	increasing	energy	visibility	perhaps	does	not	result	in	the	adoption	of	more	energy	
efficient	 behaviour.	 Findings	 from	 this	 research	 show	 that	 invisibility	 did	 constitute	 a	 barrier	 for	 the	
adoption	of	energy	efficient	behaviour,	(6.1.1.).	What	remained	to	some	extent	unclear	through	this	work	is	
what	impact,	ultimately,	would	an	increase	in	visibility	have	in	terms	of	energy	use.	The	findings	obtained	
are	in	support	of	the	literature,	(Abrahamse	et	al.,	2005;	Geller,	2002;	Martiskainen,	2007;	Staats,	Wit,	&	
Midden,	1996;	2.2.1;	2.2),	that	even	if	energy	use	becomes	visible,	the	impact	of	this	visibility	on	energy	use	
and	on	the	adoption	of	more	energy	efficient	behaviour	might	be	limited,	(6.1.1).	
9.2.3 	Financial	motivations	to	save	energy	
During	 the	 empirical	 study	 saving	 money,	 or	 reducing	 cost,	 appeared	 to	 be	 the	 main	 motivation	 for	
individuals’	to	save	energy,	(7.1.1;	7.1.2).	However,	findings	from	this	research	equally	indicate	that	this	
motivation	 directly	 competes	 with	 motivations	 of	 not	 reducing	 energy	 use,	 such	 as	 to	 maintain	 existing	
comfort	 levels,	 (7.3.2).	 Moreover,	 participants	 in	 this	 research	 appear	 to	 be	 aware	 of	 this	 competing	
situation	and	preference	for	increased	energy	use,	appearing	to	feel	comfortable	with	this	as	long	as	they	
could	afford	it,	(6.2.4;	7.1.1.).	Further	evidence	was	found	that	energy	use	is	mostly	the	result	of	a	focus	on	
the	 services	 that	 energy	 provides,	 (6.1.1),	 such	 as	 cooking,	 lighting,	 or	 enjoying	 a	 movie,	 rather	 than	
considering	the	energy	being	used,	(Goldblatt,	2005;	Martiskainen,	2007;	2.2).	This	might	be	in	particular	
problematic	as	the	number	of	home	appliances	owned	is	constantly	increasing,	as	are	the	related	practices	
to	such	appliances,	such	as	heating	or	cooling	homes,	(6.2.1;	6.2.3).	Within	this	work	it	was,	however,	not	
possible	to	clearly	understand	the	scope	of	association	between	‘practice’,	‘services’	and	‘energy	use’,	nor	
whether	this	could	influence	the	purchase	decision	towards	more	energy	efficient	home	appliances,	(6.2.4).
9.	Conclusion	
	
203	
Thus,	despite	being	reported	as	the	most	important	motivating	factor	for	saving	energy,	the	findings	from	
this	 work	 rather	 suggest	 that	 financial	 motivations	 appear	 to	 not	 be	 a	 main	 priority	 for	 adopting	 more	
energy	 efficient	 behaviour,	 (7.1.1).	 An	 exception	 to	 this	 are	 those	 people	 on	 a	 low	 income	 that	 find	
themselves	in	a	situation	of	energy	and	fuel	poverty,	to	whom	reducing	energy	bills,	thus	saving	money,	
would	be	crucial,	(6.2.4;	7.1.1.).	This	study	provided	further	evidence	the	amount	of	people	that	live	in	a	
situation	of	energy	or	fuel	poverty	might	be	higher	and	what	is	commonly	perceived	in	a	Southern	country.	
9.2.4 	Knowledge,	competence	and	self-efficacy	
Findings	from	this	research	indicate	that	participants	do	hold	a	good	level	of	information	regarding	energy	
efficient	 behaviour;	 with	 this	 level	 of	 information	 decreasing	 once	 it	 impacts	 specific	 behaviours.	 This	
suggests	the	need	for	improving	the	householders’	knowledge	on	the	specific	behaviours	they	could	adopt	
and	customizes	to	their	reality	and	needs,	as	opposed	to	general	information,	(7.2.2).	In	addition	to	this,	
most	of	the	more	energy	efficient	behaviour	appears	to	have	been	learned	during	childhood	and	through	
life	experience,	rather	than	as	a	result	of	information	received	through	any	type	of	intervention,	(7.3.1;	
8.3.3).	The	findings	also	show	that	to	encourage	the	adoption	of	more	energy	efficient	behaviour	might	
thus	 also	 require	 increasing	 knowledge,	 competence	 and	 self-efficacy	 and	 not	 simply	 provision	 of	
information	 through,	 for	 example,	 the	 design	 of	 customized	 utility	 bills,	 (8.4.2),	 the	 provision	 of	 energy	
labels,	(8.2.3),	the	provision	of	energy	meters,	(8.4.1),	or	of	tariff	structure	adoption,	(8.2.1).		
As	can	be	seen	from	both	this	work,	(7.2.2;	8.1;	8.2.3;	8.3.1;	8.3.2;	8.4)	and	the	literature,	(3.1;	3.2;	3.3;	3.4;	
4.2;	 4.4;	 4.5.),	 strategies	 of	 information-based	 interventions	 may	 not	 be	 enough	 to	 effectively	 challenge	
expectations	of	energy	needs	and	encourage	people	to	adopt	more	energy	efficient	behaviour.	
9.2.5 	Energy	efficient	behaviour	and	outcome	efficacy	
Participants	 in	 this	 research	 declared	 an,	 apparent,	 overall	 preference	 for	 ‘easy	 to	 do’	 energy	 efficient	
behaviours,	e.g.	switching	lights	off	when	not	in	use,	that	frequently	appeared	to	result	in	a	belief	of	having	
done	 their	 bit,	 or	 even	 everything	 they	 could,	 to	 save	 energy,	 which	 have	 also	 been	 an	 often-reported	
reason	 for	 not	 adopting	 additional	 energy	 efficient	 behaviour,	 (6.2.1;	 7.3.3;	 8.1).	 This	 understanding	 of	
doing	‘their	bit’	appeared	to	be	often	associated	with	a	lack	of	perceived	collective	efficacy,	be	it	within	the
9.	Conclusion	
	
204	
family	setting,	among	their	family	and	friends,	or	even	society,	(7.3.4),	and	much	in	support	of	the	work	of	
Cialdini	et	al.	(1990)	and	van	der	Pligt	(1985)	and	as	discussed	in	4.2.	This	is	to	say	that	participants	from	the	
empirical	study	often	reported	they	felt	that	they	were	alone	in	their	efforts	and	not	supported	by	family,	
friends	or	society,	to	adopt	more	energy	efficiency	behaviour.	This	negatively	impacted	their	perception	of	
the	efficacy	of	their	efforts	and	their	outcome	efficacy.	
9.3 Limitations	of	the	research	
This	research	has	a	number	of	identified	limitations.	First	of	all,	it	cannot	claim	to	be	representative	for	the	
Portuguese	 population.	 Even	 though	 the	 quantitative	 survey	 used	 representative	 sampling,	 the	 focus	
groups	were	only	conducted	in	two	different	locations	in	the	North	of	Portugal	and	consequently,	do	not	
necessarily	provide	a	representative	view	of	the	Portuguese	population.	The	fact	that	both	the	sample	of	
participants	 in	 FGs	 and	 CID	 interviews	 was	 limited	 to	 a	 range	 of	 consumers	 who	 shared	 a	 geographical	
location,	which	might	have	limited	the	diversity	of	answers.	
A	 second	 limitation	 is	 that	 the	 study	 measured	 self-reported	 intentions	 and	 willingness	 to	 act;	 but	 not	
actual	behaviour.	Responses	might,	thus,	not	be	as	accurate	as	they	could	have	been,	due	to,	for	example,	
influence	by	social	desirability,	or	other	self-report	distortions,	(such	as	recalling	difficulties),	as	is	known	
from	the	literature,	(e.g.	Darnton,	2008).	While	direct	observation	methodology	could	have	been	adopted,	
it	would	have	undermined	the	exploratory	character	of	this	research	and	the	attempt	to	allow	for	a	large	
variety	of	narratives.		
9.4 Suggested	future	research	
A	number	of	future	research	directions	could	be	identified	through	this	work	as	follows.	
Despite	the	body	of	existing	research	and	evidence	presented	through	this	work,	there	appears	to	be	still	
no	clearly	agreed	best	practice,	within	the	literature,	on	how	to	ultimately	support	the	adoption	of	more	
energy	efficient	behaviour	at	home.	Practitioners	are	equipped	with	a	range	of	intervention	strategies,	but	
the	difficulty	faced	is	to	understand	which	one	should	be	used	in	relation	to	the	vast	range	of	underlying	
and	impacting	determinants,	in	order	to	encourage	the	adoption	of	more	energy	efficient	behaviour.	While
9.	Conclusion	
	
205	
some	 previous	 research	 has	 demonstrated	 that	 certain	 intervention	 strategies	 did,	 or	 did	 not,	 produce	
changes	in	behaviour,	they	mostly	could	not	sufficiently	explain	how	change	came	about	and	led	to	the	
desired	 adoption,	 whether	 short	 or	 long-term,	 of	 more	 energy	 efficient	 behaviour.	 The	 findings	 of	 this	
research	have	challenged	the	potential	impact	of	strategies,	such	as	information	provision,	but	also	shown	
the	potential	that	community-based	initiatives	appear	to	have,	as	they	tend	to	focus	on	the	importance	of	
social	networks	for	circulating	information	and	expectations,	regarding	appropriate	behaviour.	These	are	
fields	that,	therefore,	might	be	further	explored,	for	example	through	the	use	of	smart	technologies.	
This	research	has	also	shown	that	if	the	rate	of	adoption	of	more	energy	efficient	behaviour	is	to	increase,	
that	interventions,	focusing	on	providing	information	or	financial	incentives,	are	unlikely	to	work	for	a	large	
proportion	 of	 energy	 users.	 Consideration	 might	 thus	 be	 given	 to	 exploring	 how	 self-efficacy	 could	 be	
increased	and,	most	importantly,	how	strategies	of	reduced	energy	use	developed.		
This	study	acknowledged	the	number	of	programmes	and	interventions	that	have	been	implemented	in	
Portugal	(1.7.).	Nevertheless	little	evidence	could	be	found	in	terms	of	the	impact	of	such	interventions	
within	the	scope	of	this	research,	and	thus	future	studies	might	want	to	advance	on	this.
References	
	
206	
References	
Abrahamse,	W.	(2003).	The	effect	of	tailored	information	goal	setting	and	feedback	on	household	energy	
use.	 In	 L.	 Hendrickx,	 W.	 Jager	 &	 L.	 Steg	 (Eds.),	 Human	 decision	 making	 and	 environmental	
perception.	Understanding	and	assisting	human	decision	making	in	real-life	settings	(pp.	183-201).	
Groningen:	Department	of	Psychology,	University	of	Groningen.	
Abrahamse,	W.	(2007).	Energy	conservation	through	behavioral	change:	Examining	the	effectiveness	of	a	
tailor-made	 approach.	 University	 Library	 of	 Groningen.	 Retrieved	 from	
http://dissertations.ub.rug.nl/faculties/gmw/2007/w.abrahamse/.			
Abrahamse,	 W.,	 &	 Steg,	 L.	 (2009).	 How	 do	 socio-demographic	 and	 psychological	 factors	 relate	 to	
households’	 direct	 and	 indirect	 energy	 use	 and	 savings?	 Journal	 of	 Economic	 Psychology,	 30(5),	
711-720.		
Abrahamse,	 W.,	 Steg,	 L.,	 Vlek,	 C.,	 &	 Rothengatter,	 T.	 (2005).	 A	 review	 of	 intervention	 studies	 aimed	 at	
household	energy	conservation.	Journal	of	Environmental	Psychology,	25(3),	273-291.		
Abrahamse,	 W.,	 Steg,	 L.,	 Vlek,	 Ch.,	 &	 Rotehengatter,	 T.	 (2007).	 The	 effect	 of	 tailored	 information,	 goal	
setting,	 and	 tailored	 feedback	 on	 household	 energy	 use,	 energy-related	 behaviours,	 and	
behavioural	antecedents.	Journal	of	Environmental	Psychology,	27(4),	265-276.		
ACEEE.	(n.d.).	Glossary.	Retrieved	18	of	February,	2013,	from	http://aceee.org/glossary.	
ADENE.	(2013).	Guia	da	eficiência	energética.	Lisbon:	Agência	para	a	Energia.	
ADENE.	 (n.d.).	 Planos	 e	 programas.	 Retrieved	 22	 of	 June,	 2015,	 from	 http://www.adene.pt/planos-e-
programas.		
Ajzen,	I.	(1991).	The	theory	of	planned	behavior.	Organizational	Behavior	and	Human	Decision	Processes,	
50,	179-211.		
Ajzen,	I.,	&	Fishbein,	M.	(1980).	Understanding	attitudes	and	predicting	social	behavior.	Englewood	Cliffs,	
NJ:	Prentice-Halls.	
Ajzen,	I.,	&	Madden,	T.	J.	(1986).	Prediction	of	goal-directed	behavior:	Attitudes,	intentions,	and	perceived	
behavioral	control.	Journal	of	Experimental	Social	Psychology,	22,	453-474.		
Ackermann,	M.	E.	Ackermann	(2002).	Cool	Comfort:	America's	Romance	With	Air-Conditioning.	Washington,	
D.C.	and	London:	Smithsonian	Institution	Press.	
Allen,	 J.	 B.,	 &	 Ferrand,	 J.	 L.	 (1999).	 Environmental	 locus	 of	 control,	 sympathy,	 and	 proenvironmental	
behavior.	Environment	and	Behavior,	31,	338–353.		
Anderson,	C.A.	(2007).	Belief	perseverance	Encyclopedia	of	Social	Psychology	(pp.	109-110).	Thousand	Oaks,	
CA:	Sage.	
Andreasen,	 A.	 R.	 (1995).	 Marketing	 social	 change:	 Changing	 behavior	 to	 promote	 health,	 social	
development,	and	the	environment.	San	Francisco:	Jossey-Bass.	
APA	 [American	 Psychological	 Association	 Task	 Force	 on	 the	 Interface	 Between	 Psychology	 and	 Global	
Climate	 Change].	 (2009).	 Psychology	 and	 global	 climate	 change:	 Addressing	 a	 multi-faceted	
phenomenon	 and	 set	 of	 challenges.	 Retrieved	 from	
http://www.apa.org/science/about/publications/climate-change.aspx.
References	
	
207	
Backhaus,	J.,	Breukers,	S.,	Mont,	O.,	Paukovic,	M.,	&	Mourik,	R.	(2012).	Sustainable	Lifestyles:	today's	facts	
and	tomorrow's	trends.	SPREAD	Sustainable	Lifestyles	2050	consortium	(pp.	160).	The	Netherlands:	
Energy	research	Centre	of	the	Netherlands.	
Baird,	J.	C.,	&	Brier,	J.	M.	.	(1981).	Perceptual	awareness	of	energy	requirements	of	familiar	object.	Journal	
of	Applied	Psychology,	66,	90-96.		
Baker,	S.	L.,	&	Kirsch,	I.	(1991).	Cognitive	mediators	of	pain	perception	and	tolerance.	Journal	of	Personality	
and	Social	Psychology,	61(3),	504.		
Bamberg,	 M.	 (2003).	 Positioning	 with	 Davie	 Hogan	 –	 Stories,	 Tellings,	 and	 Identities.	 In	 C.	 Daiute	 &	 C.	
Lightfoot	 (Eds.),	 Narrative	 analysis:	 Studying	 the	 development	 of	 individuals	 in	 society	 (pp.	 135-
157).	London,	UK:	Sage	Publications.	
Bamberg,	S.,	Ajzen,	I.,	&	Schmidt,	P.	(2003).	Choice	of	travel	mode	in	the	theory	of	planned	behavior:	The	
roles	of	past	behavior,	habit,	and	reasoned	action.	Basic	and	applied	social	psychology,	25(3),	175-
187.		
Bandura,	A.	(1977a).	Self-efficacy:	Toward	a	unifying	theory	of	behavioural	change.	Psychological	Review,	
94(2),	191-215.	
Bandura,	A.	(1977b).	Social	Learning	Theory.	Englewood	Cliffs,	NJ:	Prentice	Hall.	
Bandura,	A.	(1982).	Self-efficacy	mechanism	in	human	agency.	American	psychologist,	37(2),	122.		
Bandura,	A.	(1986).	Social	Foundations	of	Thought	and	Action:	A	Social	Cognitive	Theory.	Englewood	Cliffs,	
NJ:	Prentice-Hall.	
Bandura,	A.	(1990).	Selective	activation	and	disengagement	of	moral	control.	Journal	of	Social	Issues,	46,	
27-46.		
Bandura,	A.	(1992).	Observational	learning.	In	L.	R.	Squire	(Ed.),	Encyclopedia	of	learning	and	memory.	New	
York:	Macmillan.	
Barenergy	(2011).	Barriers	to	changes	in	energy	behaviour	among	end	consumers	and	households.	Final	
Report.	
Barr,	S.,	&	Gilg,	A.W.	(2006).	Sustainable	Lifestyles:	framing	environmental	action	in	and	around	the	home.	
Geoforum,	37(6),	906-920.		
BBC	 News.	 (2010).	 Climate	 scepticism	 'on	 the	 rise'.	 BBC	 poll	 shows.	 Retrieved	 08	 of	 July,	 2012,	 from	
http://news.bbc.co.uk/2/hi/8500443.stm.	
BBC	World	Service	Poll.	(2007).	All	Countries	Need	to	Take	Major	Steps	on	Climate	Change:	Global	Poll	PIPA,	
Global	Scan.	
Becker,	L.	J.	(1978).	Joint	effect	of	feedback	and	goal	setting	on	performance:	A	field	study	of	residential	
energy	conservation.	Journal	of	Applied	Psychology,	63(4),	428-433.		
Becker,	L.	J.,	Seligman,	C.,	Fazio,	R.	H.,	&	Darley,	J.	M.	(1981).	Relating	attitudes	to	residential	energy	use.	
Environment	and	Behavior,	13,	590-609.		
Bergman,	M.	M.	(2010).	On	Concepts	and	Paradigms	in	Mixed	Methods	Research.	Journal	of	Mixed	Methods	
Research,	4(3),	171-175.		
Bergman,	M.	M.	(2011).	The	Good,	the	Bad,	and	the	Ugly	in	Mixed	Methods	Research	and	Design.	Journal	of	
Mixed	Methods	Research,	5(4),	271-275.		
Berkhout,	 P.H.G.,	 Muskens,	 J.C.,	 &	 Velthuijsen,	 J.	 W.	 (2000).	 Defining	 the	 rebound	 effect.	 Energy	 Policy,	
28(6-7),	425-432.
References	
	
208	
Binswanger,	 M.	 (2001).	 Technological	 progress	 and	 sustainable	 development:	 what	 about	 the	 rebound	
effect?	Ecological	economics,	36(1),	119-132.		
Bittle,	R.	G.,	Valesano,	R.,	&	Thaler,	G.	(1979).	The	effects	of	daily	cost	feedback	on	residential	electricity	
consumption.	Behavior	Modification,	3(2),	187-202.		
Black,	J.	S.,	Stern,	P.	C.,	&	Elworth,	J.	T.	(1985).	Personal	and	contextual	influences	on	household	energy	
adaptations.	Journal	of	Applied	Psychology,	70(1),	3-21.		
Boardman,	 Brenda.	 (1991).	 Fuel	 poverty:	 from	 cold	 homes	 to	 affordable	 warmth.	 London,	 UK:	 Belhaven	
Press.	
Boardman,	Brenda.	(2010).	Fixing	Fuel	Poverty:	Challenges	and	Solutions.	London,	UK:	Earthscan.	
BPIE.	(2011).	Europe's	buildings	under	the	microscope:	Buildings	Performance	Institute	Europe	(BPIE).	
Brandon,	G.,	&	Lewis,	A.	(1999).	Reducing	household	energy	consumption:	a	qualitative	and	quantitative	
field	study.	Journal	of	Environmental	Psychology,	19(1),	75-85.		
Brehm,	J.	W.	(1972).	Responses	to	loss	of	freedom:	A	theory	of	psychological	reactance.	New	York:	General	
Learning.	
Brehm,	S.,	&	Kassin,	S.	(1996).	Social	Psychology	(3rd	ed.).	Boston:	Houghton	Mifflin	Company.	
Brook	Lyndhurst.	(2007).	Defra	Waste	&	Resources	R&D	Programme	-	Lifestyle	Scenarios:	the	Futures	for	
Waste	Composition.	Summary	Report.	A	project	for	Defra’s	WREP:	Brook	Lyndhurst	Ltd.	
Brookes,	L.	(2000).	Energy	efficiency	fallacies	revisited.	Energy	Policy,	28(6),	355-366.		
Brouwer,	 R.,	 Brander,	 L.	 M.,	 &	 van	 Beukering,	 P.	 (2008).	 “A	 convenient	 truth”:	 Air	 travel	 passengers	
willingness	to	pay	to	offset	their	CO2	emissions.	Climatic	Change,	90(3),	299-313.		
Burgess,	J.,	&	Nye,	M.	(2008).	Rematerialising	energy	use	through	transparent	monitoring	systems.	Energy	
Policy,	36(12),	4454-4459.	
Burns,	D.,	(2006)	‘Evaluation	in	complex	governance	arenas:	the	potential	of	large	system	action	research’,	
in	 B.	 Williams	 and	 I.	 Imam,	 Using	 systems	 concepts	 in	 evaluation,	 Fairhaven,	 MA:	 American	
Evaluation	Association.	
BusinessDictionary.	(n.d.).	Energy	Conservation.	Business	Dictionary.		Retrieved	12	of	February,	2013,	from	
http://www.businessdictionary.com/definition/energy-conservation.html.	
Buzar,	S.	(2007a).	Energy	Poverty	in	Eastern	Europe:	Hidden	Geographies	of	Deprivation.	Aldershot:	Ashgate.	
Buzar,	S.	(2007b).	The	‘hidden’geographies	of	energy	poverty	in	post-socialism:	between	institutions	and	
households.	Geoforum,	38(2),	224-240.		
Buzar,	 S.	 (2007c).	 When	 homes	 become	 prisons:	 the	 relational	 spaces	 of	 postsocialist	 energy	 poverty.	
Environment	and	Planning	A,	39(8),	1908-1925.		
Campbell,	C.	(1995).	The	Sociology	of	Consumption	Acknowledging	Consumption	(pp.	96-126).	London	and	
New	York:	Routledge.	
Carey,	S.	(1986).	Cognitive	science	and	science	education.	American	Psychologist,	41(10),	1123-1130.		
Carpenter,	S.	R.,	Folke,	C.,	Scheffer,	M.,	&	Westley,	F.	(2009).	Resilience:	accounting	for	the	noncomputable.	
Ecology	&	society,	14(1),	13.		
Cassiani,	S.,	Zanetti,	M.,	&	Pelá,	N.	(1992).	The	telephone	survey:	a	methodological	strategy	for	obtaining	
information.	Journal	of	Advanced	Nursing,	17,	576-581.
References	
	
209	
Chaiken,	S.,	&	Trope,	Y.	(1999).	Dual	Process	Theories	in	Social	Psychology.	New	York:	Guilford	Publications.	
Chappells,	H.	&	Shove,	E.	(2005).	Building	Research	&	Information,	33(1),	p.	32-40	p.	
Chatterton,	T.	(2011).	An	Introduction	to	Thinking	About	‘Energy	Behaviour’:	a	multi-model	approach	(pp.	
39).	London,	UK:	Department	of	Energy	and	Climate	Change.	
Cialdini,	R.	B.	(1993).	Influence	(rev):	The	Psychology	of	Persuasion:	HarperCollins.	
Cialdini,	R.	B.	(2001).	Influence:	Science	and	Practice	(4th	ed.).	Boston,	MA:	Allyn	&	Bacon.	
Cialdini,	 R.	 B.,	 Kallgren,	 C.	 A.,	 &	 Reno,	 R.	 R.	 (1991).	 A	 focus	 theory	 of	 normative	 conduct:	 A	 theoretical	
refinement	and	reevaluation	of	the	role	of	norms	in	human	behavior.	Advances	in	experimental	
social	psychology,	24(20),	1-243.		
Cialdini,	 R.	 B.,	 Reno,	 R.	 R.,	 &	 Kallgren,	 C.	 A.	 (1990).	 A	 focus	 theory	 of	 normative	 conduct:	 Recycling	 the	
concept	of	norms	to	reduce	littering	in	public	places.	Journal	of	personality	and	social	psychology,	
58(6),	1015-1026.		
Cialdini,	R.	B.,	&	Trost,	M.	R.	.	(1998).	Social	influence:	Social	norms,	conformity	and	compliance.	In	D.	T.	
Gilbert	&	S.	T.	Fiske	(Eds.),	The	handbook	of	social	psychology	(4th	ed.,	Vol.	2,	pp.	151-192).	New	
York:	McGraw-Hill.	
Clough,	P.,	and	Nutbrown,	C.	(2007)	A	student’s	guide	to	methodology.	London:	Sage	Publications.	ISBN	0	
978-1-4129-2912-7.	
Cohen,	L.,	Manion,	L.,	&	Morrison,	K.	(2000).	Research	methods	in	education	(pp.	245).	London:	Routledge	
Falmer.	
Cole,	S.	A.	(2006).	Witnessing	Creation.	Social	Studies	of	Science,	36(6),	855-860.		
Cole.	 R.	 J.	 (2011).	 Motivating	 stakeholders	 to	 deliver	 environmental	 change.	 Building	 Research	 &	
Information,	39(5),	431-435	
CCC.	 (2012).	 How	 local	 authorities	 can	 reduce	 emissions	 and	 manage	 climate	 risk	 (pp.	 96).	 London,	 UK:	
Committee	on	Climate	Change.	
Cooper,	H.	(1998).	Synthetizing	research:	a	guide	for	literature	reviews	(3rd	ed.).	Beverly	Hills,	CA:	Sage.	
Corti,	L.	(1993).	Using	diaries	in	social	research.	Social	research	update,	3(2).		
Creswell,	J.	W.	(2009).	Research	Design:	Qualitative,	Quantitative	and	Mixed	Methods	Approaches.	London:	
Sage	Publications.	
Creswell,	J.	W.,	&	Clark,	V.	L.	P.	(2007).	Designing	and	conducting	mixed	methods	research.	Thousand	Oaks,	
CA:	Sage	publications.	
Creswell,	J.	W.,	&	Miller,	D.	L.	(2000).	Determining	validity	in	qualitative	inquiry.	Theory	into	practice,	39(3),	
124-131.		
Crosbie,	T.,	&	Baker,	K.	(2010).	Energy-efficiency	interventions	in	housing:	learning	from	the	inhabitants.	
Building	Research	&	Information,	38(1),	70-79.		
Dainton,	M.,	&	Zelley,	E.	(2005).	Applying	communications	theory	for	professional	life.	Thousand	Oaks:	Sage.	
Darby,	S.	(2005).	Social	learning	and	public	policy:	Lessons	from	an	energy-conscious	village.	Energy	Policy,	
(34),	2929-2940.	
Darby,	 S.	 (2006).	 The	 Effectiveness	 of	 feedback	 on	 Energy	 Consumption:	 A	 review	 for	 DEFRA	 of	 the	
literature	 on	 metering,	 billing	 and	 direct	 displays	 (pp.	 24):	 Environmental	 Change	 Institute,	
University	of	Oxford	(available	at:	http://www.defra.gov.uk/environment/energy/research/).
References	
	
210	
Darby,	 S.	 (2010).	 Smart	 metering:	 what	 potential	 for	 householder	 engagement?,	 Building	 Research	 &	
Information,	38:5,	442-457.	
Darley,	J.	M.,	&	Latane,	B.	(1968).	Bystander	intervention	in	emergencies:	diffusion	of	responsibility.	Journal	
of	personality	and	social	psychology,	8(4p1),	377.		
Darnton,	A.	(2008).	Reference	Report:	An	overview	of	behaviour	change	models	and	their	uses	In	S.	S.	i.	G.	
Government	 Social	 Research	 (Ed.),	 GSR	 Behaviour	 Change	 Knowledge	 Review:	 Centre	 for	
Sustainable	Development,	University	of	Westminster.		
Darnton,	 A.,	 Verplanken,	 B.,	 White,	 P.,	 &	 Whitmarsh,	 L.	 E.	 (2011).	 Habits,	 Routines	 and	 Sustainable	
Lifestyles:	A	summary	report	to	the	Department	for	Environment,	Food	and	Rural	Affairs.	London,	
UK:	A.	D.	Research	and	Analysis	for	Defra.	
Dawson,	C.	(2002).	Practical	research	methods:	A	user-friendly	guide	to	mastering	research.	Oxford:	How	To	
Books	Ltd.	ISBN	1-85703-829-0.	
Dawson,	T.	L.	(2002).	New	tools,	new	insights:	Kohlberg's	moral	reasoning	stages	revisited.	International	
Journal	of	Behavior	Development,	26(2),	154-166.		
de	Dear,	R.	J.,	&	Brager,	G.	(2001).	The	adaptive	model	of	thermal	comfort	and	energy	conservation	in	the	
built	environment.	International	Journal	of	Biometeorology,	45(2),	100-108.		
de	Groot,	J.	I.,	Steg,	L.,	&	Dicke,	M.	(2007).	Morality	and	Reducing	Car	Use:	Testing	the	Norm	Activation	
Model	 of	 Prosocial	 Behavior.	 In	 F.	 Columbus	 (Ed.),	 Transportation	 Research	 Trends:	 NOVA	
Publishers.	
DECC.	(2011).	Great	Britain’s	housing	energy	fact	file	In	J.	Palmer	&	I.	Cooper	(Eds.),	(pp.	118):	Department	
of	Energy	&	Climate	Change	(DECC).	
DECC.	 (2012).	 Public	 attitudes	 tracking	 survey:	 wave	 2	 Public	 attitudes	 tracking	 survey:	 Department	 of	
Energy	&	Climate	Change	(DECC).	
DEFRA.	 (2007).	 Survey	 of	 Public	 Attitudes	 and	 Behaviours	 toward	 the	 Environment:	 2007.	 London:	
Department	for	Environment,	Food	and	Rural	Affairs	(DEFRA).	
DEFRA.	 (2008).	 A	 Framework	 for	 Pro-Environmental	 Behaviours	 Report.	 London:	 Department	 for	
Environment,	Food	and	Rural	Affairs	(DEFRA).	
Denzin,	N.,	&	Lincoln,	Y.	S.	(2002).	Handbook	of	Qualitative	Research.	London:	Sage	Publications.	
DCLG.	 (2012).	 Definitions	 of	 general	 housing	 terms.	 Definitions	 for	 local	 authorities	 compiling	 data.		
Retrieved	12	of	January,	2013,	from	https://www.gov.uk/definitions-of-general-housing-terms.	
Deutsch,	M.	(2010).	Life	Cycle	Cost	Disclosure,	Consumer	Behavior,	and	Business	Implications.	Journal	of	
Industrial	Ecology,	14(1),	103-120.		
DGEG.	 (2010).	 National	 Energy	 Characterization.	 Retrieved	 11	 of	 February,	 2012,	 from	
http://www.dgge.pt/.	
DGGE/IP-3E.	 (2004).	 Eficiência	 energética	 em	 equipamentos	 e	 sistemas	 eléctricos	 no	 sector	 residencial.	
Lisbon:	Direcção	Geral	de	Geologia	e	Energia	(DGGE).	
Dholakia,	R.	R.,	&	Dholakia,	N.	(1983).	From	social	psychology	to	political	economy:	A	model	of	energy	use	
behavior.	Journal	of	Economic	Psychology,	3,	231-247.		
Diekmann,	 A.,	 &	 Meyer,	 R.	 (2008).	 Schweizer	 Umweltsurvey	 2007.	 Dokumentation	 und	 Codebuch	 (Swiss	
Environmental	Survey	2007.	Documentation	and	code	book).	Zurich:	Professorship	for	Sociology,	
ETH.	
Dobson,	A.	(2011).	Sustainability	Citizenship	(G.	House	Ed.).	United	Kingdom:	Green	House.
References	
	
211	
Dolan,	P.;	Hallsworth,	M.;	Halpern,	D.;	King,	D.;	Vlaev,	I.	(2010).	Mindspace	-	Influencing	behaviour	through	
public	policy.	
Donn,	 J.	 (1999).	 Frustration	 sapping	 environmental	 concern,	 researcher	 says:	 Associated	 Press	 state	 and	
local	wire.	
Dwyer,	 W.	 O.,	 Leeming,	 F.	 C.,	 Cobern,	 M.	 K.,	 Porter,	 B.	 E.,	 &	 Jackson,	 J.	 M.	 (1993).	 Critical	 review	 of	
behavioral	 interventions	 to	 preserve	 the	 environment.	 Research	 since	 1980.	 Environment	 and	
Behavior,	25(5),	275-321.		
Easterby-Smith,	M.,	Thorpe,	R.,	&	Lowe,	A.	(2002).	Management	Research:	An	Introduction.	London,	UK:	
Sage	Publications.	
EEA.	(2004).	EEA	Signals	2004	-	A	European	Environment	Agency	update	on	selected	issues.	Copenhagen:	
European	Environment	Agency	(EEA),	Office	for	Official	Publications	of	the	European	Communities	
(OPOCE).	
EEA.	(2008).	Energy	and	environment	report	2008.	Copenhagen:	European	Environment	Agency	(EEA).	
EEA.	(2011).	Final	energy	consumption	by	sector	in	the	EU-27,	1990-2008.			Retrieved	12	of	February,	2012,	
from	http://www.eea.europa.eu/data-and-maps/figures/final-energy-consumption-by-sector-4.	
EEA.	 (2013).	 Achieving	 Energy	 Efficiency	 through	 behaviour	 change:	 what	 does	 it	 take?	 Copenhagen:	
European	Environment	Agency	(EEA).	
EIA.	 (2013).	 Glossary.	 U.S.	 Energy	 Information	 Administration.	 	 Retrieved	 12	 of	 February,	 2013,	 from	
http://www.eia.gov/tools/glossary/index.cfm.	
ECI.	(2005).	40%	house.	Oxford,	UK.	
Elkington,	 J.	 (1997).	 Cannibals	 with	 Forks:	 the	 Triple	 Bottom	 Line	 of	 21st	 Century	 Business.	 New	 York:	
Capstone	Publishing	Ltd.	
Energaia	(2008).	Energyprofiler:	Perfil	energético	do	sector	residencial.	ENERGAIA,	Agência	de	Energia	do	
Sul	da	Área	Metropolitana	do	Porto.	
Energy	Saving	Trust.	(2011).	The	rise	of	the	machines:	a	review	of	energy	using	products	in	the	home	from	
the	1970s	to	today.	London:	Energy	saving	Trust.	
Energy	Saving	Trust.	(2012).	Powering	the	nation:	household	electricity	using	habits	revealed.	London,	UK:	
Energy	Saving	Trust.	
Energyprofiler.	 (2011).	 Transformar	 atitudes	 em	 ação:	 Perfil	 Energético	 do	 Setor	 Residencial:	 ENERGAIA,	
Agência	de	Energia	do	Sul	da	Área	Metropolitana	do	Porto.	
Eurobarometer.	 (2011a).	 Special	 Eurobarometer	 365.	 Attitudes	 of	 European	 citizens	 towards	 the	
environment.	
Eurobarometer.	(2011b).	Special	Eurobarometer	372.	Climate	Change.		
European	 Commission.	 (2010).	 EUR	 24283	 –	 Energy-efficient	 Buildings	 PPP	 Multi-annual	 Roadmap	 and	
longer	term	strategy.	Luxembourg:	Publications	Office	of	the	European	Union.	
European	 Commission	 (n.d.).	 Energy	 efficiency	 directive.	 Retrieved	 19	 of	 June,	 2015,	 from	
http://ec.europa.eu/energy/en/topics/energy-efficiency/energy-efficiency-directive.		
Eurostat.	(2007).	Statistics	on	income,	social	inclusion	and	living	conditions	-	Ad-hoc	modules	(2007	module:	
Housing	 conditions).	 Your	 key	 to	 European	 statistics.	 	 Retrieved	 10	 of	 July,	 2013,	 from	
http://epp.eurostat.ec.europa.eu/portal/page/portal/income_social_inclusion_living_conditions/d
ata/ad_hoc_modules
References	
	
212	
Eurostat.	 (2011).	 	 	 Energy	 Statistics	 Data.	 Retrieved	 1	 of	 October,	 2011,	 from		
http://epp.eurostat.ec.europa.eu/portal/page/portal/energy/data/database	
Eurostat.	(2013).	Inability	to	keep	home	adequately	warm	(source:	SILC).	Retrieved	8	of	July,	2013,	from	
http://appsso.eurostat.ec.europa.eu/nui/show.do?dataset=ilc_mdes01&lang=en	
Eurostat.	 (2015).	 Consumption	 of	 energy.	 Retrieved	 19	 of	 June,	 2015,	 from	
http://ec.europa.eu/eurostat/statistics-explained/index.php/Consumption_of_energy.		
Eurostat.	 (n.d.).	 Statistics	 explained.	 Energy	 price	 statistics.	 Retrieved	 14	 of	 July,	 2013,	 from	
http://epp.eurostat.ec.europa.eu/statistics_explained/index.php/Energy_price_statistics#Natural_
gas_prices_for_industrial_consumers	
Eurowinter	 Group.	 (1997).	 Cold	 exposure	 and	 winter	 mortality	 from	 ischaemic	 heart	 disease,	
cerebrovascular	disease,	respiratory	disease,	and	all	causes	in	warm	and	cold	regions	of	Europe.	
The	Lancet,	349(9062),	1341-1346.		
ERSE.	(2007).	Plano	de	promoção	da	eficiência	no	consumo	de	energia	elétrica	para	2008.	Lisbon:	Entidade	
Reguladora	dos	Serviços	Energético.	
ERSE.	 (2008).	 Medidas	 aprovadas	 PPEC	 08:	 Plano	 de	 promoção	 da	 eficiência	 no	 consumo	 de	 energia	
eléctrica	para	2008.	Lisbon:	Entidade	Reguladora	dos	Serviços	Energético.		
ERSE.	 (2009).	 Plano	 de	 promoção	 da	 eficiência	 no	 consumo	 de	 energia	 elétrica	 para	 2009-2010.	 Lisbon:	
Entidade	Reguladora	dos	Serviços	Energético.	
ERSE.	 (2010).	 Plano	 de	 promoção	 da	 eficiência	 no	 consumo	 de	 energia	 elétrica	 para	 2011-2012.	 Lisbon:	
Entidade	Reguladora	dos	Serviços	Energético.	
ERSE.	 (n.d.).	 Medidas	 em	 Implementação.	 Retrieved	 22	 of	 June,	 2015,	 from	
http://www.erse.pt/pt/planodepromocaodaeficiencianoconsumoppec/edicoesPPEC/siteppec1112
/medidasimplementacao/Paginas/default.aspx.	
FAI	(n.d.).	Fundo	de	apoio	à	inovação.	Retrieved	25	of	June,	2015,	from	http://fai.pt/o-fai/.		
Feather,	N.	T.	(1990).	The	psychological	impact	of	unemployment.	New	York:	Springer.	
FEE	 (n.d.).	 Fundo	 de	 eficiência	 energética.	 Retrieved	 25	 of	 June,	 2015,	 from	 http://fee.adene.pt/o-que-
e/Paginas/default.aspx.		
Feenstra,	C.F.J.,	Backhaus,	J.,	&	Heiskanen,	E.	(2009).	How	to	change	consumers’	energy-related	behaviour?	
Improving	 demand	 side	 management	 programmes	 via	 an	 action	 research	 approach.	 Paper	
presented	 at	 the	 First	 European	 Conference	 on	 Energy	 and	 Behaviour,	 Maastricht,	 The	
Netherlands.		
Feinberg,	M.,	&	Willer.,	R.	(2010).	The	Good	of	Gossip?	The	Benefits	of	this	Unlikely	Prosocial	Behavior.	
Berkeley:	Department	of	Psychology.	University	of	California.	
Festinger,	L.	(1957).	A	Theory	of	Cognitive	Dissonance.	Stanford,	CA:	Stanford	University	Press.	
Fischer,	 C.	 (2008).	 Feedback	 on	 household	 electricity	 consumption:	 a	 tool	 for	 saving	 energy?	 Energy	
efficiency,	1(1),	79-104.		
Folke,	C.	(2006).	Resilience:	The	Emergence	of	a	Perspective	for	Social-Ecological	Systems	Analyses.	Global	
Environmental	Change,	16,	253-267.		
Future	Foundation.	(2006).	Energy	Efficiency	-	Public	attitude,	private	action:	Logica.	
Galli,	A.,	Kitzes,	J.,	Wermer,	P.,	Wackernagel,	M.,	Niccolucci,	V.,	&	Tiezzi,	E.	(2007).	An	exploration	of	the	
mathematics	behind	the	ecological	footprint.	International	Journal	of	Ecodynamics,	2(4),	250–257.
References	
	
213	
Gardner,	G.	T.,	&	Stern,	P.	C.	(2002).	Environmental	Problems	and	Human	Behavior	(2nd	ed.).	Boston,	MA:	
Pearson	Custom	Publishing.	
Gardner,	G.	T.,	&	Stern,	P.	C.	(2008).	The	short	list:	The	most	effective	actions	US	households	can	take	to	
curb	climate	change.	Environment:	Science	and	Policy	for	Sustainable	Development,	50(5),	12-25.		
Gärling,	T.,	Eek,	D.,	Loukopoulos,	P.,	Fujii,	S.,	Johansson-Stenman,	O.,	Kitamura,	R.,	Vilhelmson,	B.	(2002).	A	
conceptual	 analysis	 of	 the	 impact	 of	 travel	 demand	 management	 on	 private	 car	 use.	 Transport	
Policy,	9(1),	59-70.		
Garvey,	 James.	 (2009).	 We	 broke	 it.	 So	 we	 own	 it.	 The	 Guardian.	
http://www.theguardian.com/commentisfree/cif-green/2009/sep/07/climate-change-10-10	
Gascoigne,	 C.,	 Morgan,	 K.,	 Gross,	 H.,	 &	 Goodwin,	 J.	 (2010).	 Reducing	 the	 health	 risks	 of	 severe	 winter	
weather	among	older	people	in	the	United	Kingdom:	an	evidence-based	intervention.	Ageing	&	
Society,	30,	275-297.		
Gass,	R.	H.,	&	Seiter.,	J.	S.	(2003).	Persuasion,	Social	Influence,	and	Compliance	Gaining.	Boston:	Pearson	
Education,	Inc.	
Gatersleben,	 B.,	 Steg,	 L.,	 &	 Vlek,	 C.	 (2002).	 The	 measurement	 and	 determinants	 of	 Environmentally	
significant	consumer	behaviour.	Environment	and	Behaviour,	34(3),	335-362.		
Gatersleben,	B.,	&	Vlek,	C.	(1998).	Household	Consumption,	Quality	of	Life	and	Environmental	Impacts:	A	
Psychological	 Perspective	 and	 Empirical	 Study.	 In	 T.	 S.	 Uiterkamp	 (Ed.),	 Green	 Households?	 (pp.	
141-183).	London:	Earthscan.	
Gatersleben,	B.C.M.	(2000).	Sustainable	household	metabolism	and	quality	of	life:	Examining	the	perceived	
social	 sustainability	 of	 environmentally	 sustainable	 household	 consumption	 patterns.	 (PhD),	
University	of	Groningen,	Groningen,	the	Netherlands.				
Geller,	E.	S.	(1981).	Evaluating	energy	conservation	programs:	Is	verbal	report	enough?	Journal	of	Consumer	
Research,	8,	331–335.		
Geller,	E.	S.	(1992).	It	takes	more	than	information	to	save	energy.	American	Psychologist,	47(6),	814-815.		
Geller,	E.	S.	(2002).	The	challenge	of	increasing	proenvironmental	behavior.	In	R.	B.	Betchel	&	A.	Churchman	
(Eds.),	Handbook	of	environmental	psychology	(pp.	525-540).	New	York:	John	Wiley	&	Sons.	
Geller,	E.	S.,	Berry,	T.	D.,	Ludwig,	T.	D.,	Evans,	R.	E.,	Gilmore,	M.	R.,	&	Clarke,	S.	W.	(1990).	A	conceptual	
framework	for	developing	and	evaluating	behavior	change	interventions	for	injury	control.	Health	
Education	Research,	5(2),	125-137.		
Geller,	E.	S.,	Winett,	R.	A.,	&	Everett,	P.	B.	(1982).	Preserving	the	environment:	New	strategies	for	behavior	
change.	Elmsford,	NY:	Pergamon.	
Geller,	H.,	Harrington,	P.,	Rosenfeld,	A.	H.,	Tanishima,	S.,	&	Unander,	F.	(2006).	Polices	for	increasing	energy	
efficiency:	Thirty	years	of	experience	in	OECD	countries.	Energy	Policy,	34(5),	556-573.		
Gerdes,	 J.	 (2009).	 Energy	 Efficiency	 Policies	 and	 Measures	 in	 The	 Netherlands.	 Petten:	 ECN,	 	 ODYSSEE-
MURE,	Intelligent	Energy	Europe.	
Gibbs,	Anita.	(1997).	Focus	groups.	Social	research	update,	19(8).		
Giddens,	A.	(1984).	The	Constitution	of	Society	–	outline	of	the	theory	of	structuration.	Berkeley	and	Los	
Angeles:	University	of	California	Press.	
Gifford,	 R.,	 Iglesias,	 F.,	 &	 Casler,	 J.	 (2008).	 Psychological	 barriers	 to	 pro-environmental	 behavior:	 The	
development	 of	 a	 scale.	 Paper	 presented	 at	 the	 Annual	 meeting	 of	 the	 Canadian	 Psychological	
Association,	Montreal,	QC.
References	
	
214	
Giorgi,	S.,	Fell,	D.,	Austin,	A.,	&	Wilkins,	C.	(2009).	EV0402:	public	understanding	of	links	between	climate	
change	and	(i)	food	and	(ii)	energy	use:	final	report.	A	report	to	the	Department	for	Environment,	
Food	and	Rural	Affairs.	London:	Brook	Lyndhurst	&	Defra.	
Glasersfeld,	E.	von	(1989).	“Cognition,	Construction	of	Knowledge	and	Teaching.”	Synthese,	80(1),	121-140.		
Glasersfeld,	 E.	 von	 (1990).	 “Environment	 and	 Education.”	 In	 L.P.	 Steffe	 &	 T.	 Wood	 (eds.),	 Transforming	
Children’s	 Mathematics	 Education:	 International	 Perspectives,	 (pp.	 200-215).	 Hillsdale,	 NJ:	
Lawrence	Erlbaum.	
Golafshani,	N.	(2003).	Understanding	Reliability	and	Validity	in	Qualitative	Research.	The	Qualitative	Report,	
8(4),	597-607.		
Goldblatt,	David	L.	(2005).	Sustainable	Energy	Consumption	and	Society		-	Personal,	Technological,	or	Social	
Change?	Washington	DC,	USA:	Springer.	
Gottron,	F.	(2001).	Energy	Efficiency	and	the	Rebound	Effect:	Does	Increasing	Efficiency	Decrease	Demand	
CRS	Report	for	Congress	(pp.	1-4).	
Green	Alliance.	(2011).	Green	Alliance	policy	insight.	
Grier,	S.,	&	Bryant,	C.	(2005).	Social	marketing	in	public	health.	Public	Health,	26,	319-339.		
Grist,	M.	(2010).	Changing	the	Subject,	How	new	ways	of	thinking	about	human	behaviour	might	change	
politics,	policy	and	practice.	London:	RSA.	
Grubb,	M.	J.	(1990).	Communication	energy	efficiency	and	economic	fallacies.	Energy	Policy,	18(8),	783-785.		
Guagnano,	G.	A.	(2001).	Altruism	and	market-like	behavior:	An	analysis	of	willingness	to	pay	for	recycled	
paper	products.	Population	and	Environment,	22,	425-438.		
Guertin,	C.,	Kumbhakar,	S.,	&	Duraiappah,	A.	(2003).	Determining	Demand	for	Energy	Services:	Investigating	
income	-	driven	behaviours:	International	Institute	for	Sustainable	Development.	
Hardin,	G.	(1968).	The	Tragedy	of	the	Commons.	Science,	New	Series,	162(3859),	1243-1249.		
Hargreaves,	T.	(2012).	Opening	the	black	box	of	the	household:	Understanding	how	householders	interact	
with	feedback	from	smart	energy	monitors	3S	Working	Paper.	Norwich.	
Hargreaves,	 T.,	 Nye,	 M.,	 &	 Burgess,	 J.	 (2010).	 Making	 energy	 visible:	 A	 qualitative	 field	 study	 of	 how	
householders	 interact	 with	 feedback	 from	 smart	 energy	 monitors.	 Energy	 Policy,	 38(10),	 6111-
6119.		
Harrington,	B.	E.,	Heyman,	B.,	Merleu-Ponty,	N.,	Stockton,	H.,	Ritchie,	N.,	&	Heyman,	A.	(2005).	Keeping	
warm	and	staying	well:	findings	from	the	qualitative	arm	of	the	Warm	Homes	Project.	Health	&	
social	care	in	the	community,	13(3),	256-267.		
Hastings,	 G.,	 &	 Saren,	 M.	 (2003).	 The	 Critical	 Contribution	 of	 Social	 Marketing:	 Theory	 and	 Application.	
Marketing	Theory,	3(3),	305-322.		
Hastings,	G.B.,	&	Haywood,	A.J.	(1991).	Social	marketing	and	communication	in	health	promotion.	Health	
Promotion	International,	6,	135-145.		
Healy,	J.	D.	(2003).	Excess	winter	mortality	in	Europe:	a	cross	country	analysis	identifying	key	risk	factors.	
Journal	of	Epidemiology	and	Community	Health,	57(10),	784-789.		
Healy,	J.	D.	(2004).	Housing,	Fuel	Poverty	And	Health:	A	Pan-European	Analysis.	London:	Ashgate.	
Heberlein,	 T.	 A.,	 &	 Warriner,	 G.	 K.	 .	 (1983).	 The	 influence	 of	 price	 and	 attitude	 on	 shifting	 residential	
electricity	consumption	from	on-to	off-peak	periods.	Journal	of	Economic	Psychology,	4(1),	107-
130.
References	
	
215	
Heiskanen,	E.,	Johnson,	M.,	&	Vadovics,	E.	(2009).	Creating	Lasting	Change	in	Energy	Use	Patterns	through	
Improved	User	Involvement.	Paper	presented	at	the	Joint	Actions	on	Climate	Change	Conference,	
Aalborg,	Denmark.	
Heiskanen,	E.,	Mourik,	R.,	Feenstra,	Y.,	&	Pariag,	J.	(2009).	BEYOND	INDIVIDUAL	BEHAVIOURAL	CHANGE	–	
WHY	AND	HOW?	European	council	for	an	energy	efficient	economy	(ECEEEE),	Energy	Efficiency	and	
Behaviour.	
http://www.eceee.org/library/conference_proceedings/EE_and_Behaviour/2009/Panel_7/7.702	
Helmig,	B.,	&	Thaler,	J.	(2010).	On	the	effectiveness	of	social	marketing	–	what	do	we	really	know?	Journal	
of	Nonprofit	&	Public	Sector	Marketing,	22(4),	264-287.		
Herring,	H.	(2006).	Energy	efficiency	-	a	critical	view.	Energy,	31(1),	10-20.		
Higgins,	E.	T.	(1987).	Self-discrepancy:	a	theory	relating	self	and	affect.	Psychological	review,	94(3),	319-340.		
Hitchings,	R.	(2009).	Studying	thermal	comfort	in	context.	Building	Research	and	Information,	37(1),	89-94.		
Homans,	J.	(1958).	Social	Behavior	as	Exchange.	American	Journal	of	Sociology,	63,	597-606.		
Huebner,	 Gesche	 M.,	 Cooper,	 Justine,	 &	 Jones,	 K.	 (2011).	 Energy	 saving	 practices,	 barriers	 against	 and	
reasons	 for	 change	 among	 social	 housing	 tenants.	 Paper	 presented	 at	 the	 Research	 student's	
conference	on	"Buildings	don't	use	energy,	people	do?"	-	domestic	energy	use	and	CO2	emissions	
in	existing	dwellings,	Bath,	UK.	
Hussey,	J.,	&	Hussey,	R.	(1997).	Business	Research:	A	Practical	Guide	for	Undergraduate	and	Postgraduate	
Students.	London:	Macmillan.	
INE.	(2011).	Anuário	Estatístico	de	Portugal	2010.	Lisbon:	Instituto	Nacional	de	Estatística,	I.P.	(INE).	
INE	 (2012).	 Orçamentos	 Familiares	 -	 Inquérito	 às	 despesas	 das	 famílias	 -	 2010	 /	 2011.	 Retrieved	
28/10/2013,	 from	 Instituto	 Nacional	 de	 Estatística	
http://www.ine.pt/xportal/xmain?xpid=INE&xpgid=ine_publicacoes&PUBLICACOESpub_boui=1415
77698&PUBLICACOESmodo=2&xlang=pt.	
INE	 I.P./DGEG.	 (2011).	 Inquérito	 ao	 Consumo	 de	 Energia	 no	 Sector	 Doméstico	 2010	 Estatísticas	 Oficiais.	
Lisbon,	Portugal.	
IPCC.	(2007).	Climate	Change	2007	-	Impacts,	Adaptation	and	Vulnerability:	Working	Group	II	contribution	to	
the	Fourth	Assessment	Report	of	the	IPCC	(M.	L.	Parry,	O.	F.	Canziani,	J.	P.	Palutikof,	P.	J.	van	der	
Linden	&	C.	E.	Hanson	Eds.	1st	ed.).	Cambridge,	UK:	Cambridge	University	Press.	
IPPR.	(2009).	Addressing	Climate	Change	through	Sustainable	Development.	U.S.	Department	of	State	e-
journal	USA	-	Climate	Change	Perspectives.	www.ippr.org	
IUCN,	 UNEP,	 &	 WWF.	 (1991).	 Caring	 for	 the	 Earth:	 A	 Strategy	 for	 Sustainable	 Living.	 London:	 World	
Conservation	Union	(IUCN),	United	Nations	Environment	Programme	(UNEP),	World	Wide	Fund	for	
Nature	(WWF).	
Jackson,	T.	(2005).	Motivating	Sustainable	Consumption:	a	review	of	evidence	on	consumer	behaviour	and	
behavioural	change:	University	of	Surrey.	
Jager,	W.,	Janssen,	M.,	Vries,	H.	D.,	Greef,	J.	D.,	&	Vlek,	C.	(2000).	Behaviour	in	commons	dilemmas:	Homo	
economicus	 and	 Homo	 psychologicus	 in	 an	 ecological-economic	 model.	 Ecological	 Economics,	
35(3),	357-379.		
Janda,	K.	B.	(2011).	Buildings	don't	use	energy:	people	do,	Architectural	Science	Review,	54(1),	15-22	
Jeannerod,	M.	(2003).	The	mechanism	of	self-recognition	in	humans.	Behavioural	brain	research,	142(1),	1-
15.
References	
	
216	
Kahneman,	 D.,	 &	 Tversky,	 A.	 (1979).	 Prospect	 theory:	 An	 analysis	 of	 decision	 under	 risk.	 Econometrica:	
Journal	of	the	Econometric	Society,	47(2),	263-291.		
Kaplan,	S.	(2000).	New	ways	to	promote	proenvironmental	behavior:	Human	nature	and	environmentally	
responsible	behavior.	Journal	of	social	issues,	56(3),	491-508.		
Kates,	 R.	 W.,	 Clark,	 W.	 C.,	 Corell,	 R.,	 Hall,	 J.	 M.,	 Jaeger,	 C.	 C.,	 Lowe,	 I.,	 Svedin,	 U.	 (2001).	 Sustainability	
science.	Science,	New	Series,	292(5517),	641-642.		
Kempton,	W.,	Boster,	J.	S.,	&	Hartley,	J.	A.	(1995).	Environmental	Values	in	American	Culture.	Cambridge,	
MA:	The	MIT	Press.	
Kempton.	W.,	&	Montgomery,	L.	(1982).	Folk	quantification	of	energy.	Energy	7(10),	917-927.	
Kempton,	 W.,	 Reynolds,	 C.,	 Fels,	 M.,	 &	 Hull,	 D.	 (1992).	 Utility	 control	 of	 residential	 cooling:	 resident-
perceived	effects	and	potential	program	improvements.	Energy	and	buildings,	18(3),	201-219.		
Kennedy,	L.	(2011).	Sustainable	Development.	louiskennedy	-	Just	another	WordPress.com	site.		Retrieved	5	
of	February,	2012,	from	http://louiskennedy.wordpress.com/2011/01/26/back-again/	
Khazzoom,	 J.	 Daniel.	 (1980).	 Economic	 Implications	 of	 Mandated	 Efficiency	 Standards	 for	 Household	
Appliances.	The		Energy	Journal,	1(4),	21-40.		
Kitzes,	J.,	Galli,	A.,	Bagliani,	M.,	Barrett,	J.,	Dige,	G.,	Ede,	S.,	Wiedmann,	T.	(2009).	A	research	agenda	for	
improving	national	Ecological	Footprint	accounts.	Ecological	Economics,	68(7),	1991-2007.		
Knott,	David,	Muers,	Stephen,	&	Aldridge,	Stephen.	(2008).	Achieving	Culture	Change:	A	Policy	Framework,	
A	discussion	paper	by	the	Strategy	Unit	(pp.	138).	London:	Strategy	Unit,	Cabinet	Office.	
Kollmuss,	A.,	&	Agyeman,	J.	(2002).	Mind	the	gap:	why	do	people	act	environmentally	and	what	are	the	
barriers	to	pro-environmental	behavior?	Environmental	Education	Research,	8(3),	239-260.		
Kollock,	P.	(1998).	Social	Dilemmas:	The	Anatomy	of	Cooperation.	American	Review	of	Sociology,	24,	183-
214.		
Kotler,	P.,	Roberto,	E.	L.	,	&	Roberto,	N.	.	(1989).	Social	marketing:	strategies	for	changing	public	behavior:	
Free	Press.	
Kotler,	P.,	&	Zaltman,	G.	(1971).	Social	marketing:	an	approach	to	planned	social	change.	The	Journal	of	
Marketing,	35(3),	3-12.		
KPMG.	 (2012).	 Expect	 the	 unexpected:	 Building	 business	 value	 in	 a	 changing	 world.	
http://www.kpmg.com/global/en/issuesandinsights/articlespublications/pages/building-business-
value.aspx	
Kurz,	 T.	 (2002).	 The	 psychology	 of	 environmentally	 sustainable	 behavior:	 Fitting	 together	 pieces	 of	 the	
puzzle.	Analyses	of	Social	Issues	and	Public	Policy,	2(1),	257-278.		
Leal	Filho,	W.	(2011).	About	the	Role	of	Universities	and	Their	Contribution	to	Sustainable	Development.	
Higher	Education	Policy,	24(4),	427-438.		
Leedy,	P.,	&	Ormrod,	J.	E.	(2001).	Practical	research:	Planning	and	design	(7th	ed.).	Upper	Saddle	River,	New	
Jersey:	Prentice-Hall.	
Lehman,	P.	K.,	&	Geller,	E.	S.	(2004).	Behavior	analysis	and	environmental	protection:	accomplishments	and	
potential	for	more.	Behavior	and	Social	Issues,	13(1),	13-32.		
Leiserowitz,	A.	(2007).	Public	Perception,	Opinion	and	Understanding	of	Climate	Change	–	Current	Patterns,	
Trends	and	Limitations	Human	Development	Report	2007/2008	-	Fighting	climate	change:	Human	
solidarity	in	a	divided	world.
References	
	
217	
Leiserowitz,	A.,	Maibach,	E.,	&	Roser-Renouf,	C.	(2009).	Saving	Energy	at	Home	and	on	the	Road:	A	Survey	of	
Americans’	 Energy	 Saving	 Behaviors,	 Intentions,	 Motivations,	 and	 Behaviors.	 Yale	 Project	 on	
Climate	Change.			
Leiserowitz,	A.,	Maibach,	E.,	Roser-Renouf,	C.,	&	Smith,	N.	(2011a).	Climate	change	in	the	American	Mind:	
Americans’	 global	 warming	 beliefs	 and	 attitudes	 in	 May	 2011.	 In	 Y.	 P.	 o.	 C.	 C.	 Yale	 Project	 on	
Climate	Change	Communication	(Ed.).	New	Haven,	CT:	University	and	George	Mason	University.	
Leiserowitz,	A.,	Maibach,	E.,	Roser-Renouf,	C.,	Smith,	N.,	&	Hmielowski,	J.	D.	(2011b).	Climate	change	in	the	
American	Mind:	Public	support	for	climate	&	energy	policies	in	November	2011.	New	Haven,	CT:	
Yale	University	and	George	Mason	University.	
Lewis,	D.	(1969).	Convention:	A	Philosophical	Study.	Cambridge:	Harvard	University	Press.	
Lindenberg,	S.,	&	Steg,	L.	(2007).	Normative,	gain	and	hedonic	goal	frames	guiding	environmental	behavior.	
Journal	of	Social	issues,	63(1),	117-137.		
Linville,	P.W.,	&	Fischer,	G.W.	(1991).	Preferences	for	separating	and	combining	events:	a	social	application	
of	prospect	theory	and	the	mental	accounting	model.	Journal	of	Personality	and	Social	Psychology,	
60,	5-23.		
Litoselliti,	L.	(2003).	Using	Focus	Group	in	Research:	Continuum.	
Lomas,	K.	J.	(2010).	Editorial:	Carbon	reduction	in	existing	buildings:	A	transdisciplinary	approach.	Building		
Research	and	Information,	38(1),	1-11.	
Lorenzoni,	 I.,	 &	 Pidgeon,	 N.	 F.	 (2006).	 Public	 views	 on	 climate	 change:	 European	 and	 USA	 perspectives.	
Climatic	Change,	77(1-2),	73-95.		
Lovins,	A.	B.	(1998).	Further	comments	on	red	herrings.	Letter	to	the	New	Scientist(2152),	18.		
Lovins,	A.	B.,	Henly,	J.,	Ruderman,	H.,	&	Levine,	M.	D.	(1988).	Energy	saving	resulting	from	the	adoption	of	
more	efficient	appliances:	another	view;	a	follow-up.	Energy	Journal,	9(2),	155.		
Lutzenhiser,	 L.	 (1993).	 Social	 and	 behavioral	 aspects	 of	 energy	 use.	 Annual	 Review	 of	 Energy	 and	 the	
Environment,	18(1),	247-289.		
Lutzenhiser,	L.	(2002).	Marketing	Household	Energy	Conservation:	The	Message	and	the	Reality.	In	T.	Dietz	
&	P.	C.	Stern	(Eds.),	New	Tools	for	Environmental	Protection:	Education,	Information,	and	Voluntary	
Measures.	Washington,		D.C.:	National	Academy	of	Sciences.	
Maddux,	J.	E.	(1995).	Self-Efficacy	theory:	An	introduction.	In	J.	E.	Maddux	(Ed.),	Self-Efficacy,	Adaptation,	
and	Adjustment:	Theory,	Research,	and	Application	(pp.	3-33).	New	York:	Plenum	Press.	
Magalhães,	S.,	&	Leal,	V.	(2012).	EPBD	assessment	as	a	tool	for	fuel	poverty	estimation.	Paper	presented	at	
the	IAIA12,	Porto,	Portugal.	
Maibach,	E.,	Roser-Renouf,	C.,	&	Leiserowitz,	A.	(2009).	Global	Warming’s	Six	Americas	2009:	An	audience	
segmentation.	New	Haven,	CT:	Yale	Project	on	Climate	Change,		George	Mason	University	Center	
for	Climate	Change	Communication.	
Maréchal,	 K.	 (2010).	 Not	 irrational	 but	 habitual:	 The	 importance	 of	 "behavioural	 lock-in"	 in	 energy	
consumption.	Ecological	Economics,	69(5),	1104-1114.		
Marshall,	 G.,	 &	 Lynas,	 M.	 (2003).	 Why	 we	 don't	 give	 a	 damn	 from	
http://www.newstatesman.com/node/146820	
Martiskainen,	M.	(2007).	Affecting	consumer	behaviour	on	energy	demand.	Brighton,	East	Sussex:	University	
of	Sussex.
References	
	
218	
Marx,	 S.	 M.,	 Weber,	 E.	 U.,	 Orlove,	 B.	 S.,	 Leiserowitz,	 A.,	 Krantz,	 D.	 H.,	 Roncoli,	 C.,	 &	 Phillips,	 J.	 (2007).	
Communication	and	mental	processes:	Experiential	and	analytic	processing	of	uncertain	climate	
information.	Global	Environmental	Change,	17(1),	47-58.		
Matthies,	E.,	Klöckner,	C.	A.,	&	Preißner,	C.	L.	(2006).	Applying	a	modified	moral	decision	making	model	to	
change	habitual	car	use:	how	can	commitment	be	effective?	Applied	Psychology,	55(1),	91-106.		
McCalley,	L.	T.,	&	Midden,	C.	J.	H.	(2002).	Energy	conservation	through	product-integrated	feedback:	The	
roles	of	goal-setting	and	social	orientation.	Journal	of	Economic	Psychology,	23(5),	589–603.		
McCarty,	 John	 A.,	 &	 Shrum,	 L.	 J.	 (1993).	 A	 Structural	 Equation	 Analysis	 of	 the	 Relationships	 of	 Personal	
Values,	 Attitudes	 and	 Beliefs	 about	 Recycling,	 and	 the	 Recycling	 of	 Solid	 Waste	 Products.	 In	 L.	
McAlister	&	M.	Rothschild	(Eds.),	Advances	in	Consumer	Research	(Vol.	20,	pp.	641-646).	Provo,	UT:	
Association	for	Consumer	Research.	
McKenzie-Mohr,	 D.	 (2000).	 New	 ways	 to	 promote	 proenvironmental	 behavior:	 Promoting	 sustainable	
behavior:	 An	 introduction	 to	 community-based	 social	 marketing.	 Journal	 of	 Social	 Issues,	 56(3),	
543-554.		
McKenzie-Mohr,	 D.,	 &	 Smith,	 W.	 (1999).	 Fostering	 sustainable	 behavior:	 An	 introduction	 to	 community-
based	social	marketing	(2nd	ed.).	Gabriola	Island,	British	Columbia,	Canada:	New	Society.	
McMahon,	T.	(2007)	‘Is	reflective	practice	synonymous	with	action	research?’,	Educational	Action	Research,	
Vol.7(1),	pp.163	-	169.	
McMakin,	A.	H.,	Malone,	E.	L.,	&	Lundgren,	R.	E.	(2002).	Motivating	residents	to	conserve	energy	without	
financial	incentives.	Environment	and	Behavior,	34(6),	848-863.		
McMichael,	 A.,	 Woodruff,	 R.,	 &	 Hales,	 S.	 (2006).	 Climate	 change	 and	 human	 health:	 present	 and	 future	
risks.	The	Lancet,	367(9513),	859-869.		
Merton,	R.,	&	Kendall,	P.	(1987).	The	Focused	Interview.	American	Journal	of	Sociology,	51,	541-557.		
Middlemiss,	 L.	 (2008).	 Influencing	 individual	 sustainability:	 a	 review	 of	 the	 evidence	 on	 the	 role	 of	
community-based	 organisations.	 International	 Journal	 of	 Environment	 and	 Sustainable	
Development,	7(1),	78-93.		
Mill,	J.	S.	(1836).	On	the	Definition	of	Political	Economy,	and	on	the	Method	of	Investigation	Proper	to	It.	
London	and	Westminster	Review.		
Miller,	 G.	 R.	 (2002).	 On	 Being	 Persuaded:	 Some	 Basic	 Distinctions.	 In	 J.	 P.	 Dillard	 &	 M.	 Pfau	 (Eds.),	 The	
Persuasion	Handbook:	Developments	in	Theory	and	Practice	(pp.	3-16).	Thousand	Oaks,	CA:	Sage.	
Mischler,	E.	G.	(1986).	Research	Interviewing:	Context	and	Narrative:	Harvard	University	Press.	
Morgan,	D.	(1998).	The	Focus	Group	Guidebook.	London:	Sage	Publications.	
Morgan,	D.	(2007).	Paradigms	Lost	and	Pragmatism	Regained	:	Methodological	Implications	of	Combining	
Qualitative	and	Quantitative	Methods.	Journal	of	Mixed	Methods	Research,	1,	48-76.		
Morgan,	D.	L.,	Krueger,	R.	A.,	&	King,	J.	A.	(1998).	Analyzing	and	Reporting	Focus	Group	Results.	London,	UK:	
Sage	Publications.	
Morgan,	M.	G.,	Fischhoff,	B.,	Bostrom,	A.,	&	Atman,	C.	J.	(2002).	Risk	Communication:	A	Mental	Models	
Approach.	Cambridge:	Cambridge	University	Press.	
Morse,	J.	M.	(2003).	Principles	of	mixed	methods	and	multimethod	reseacrh	method.	In	A.	Tashakkori	&	C.	
Teddlie	(Eds.),	Handbook	of	mixed	methods	in	social	&	behavioral	research	(pp.	189-208).	London:	
Sage	Publications.
References	
	
219	
Moser,	 S.	 C.	 (2007).	 More	 bad	 news:	 The	 risk	 of	 neglecting	 emotional	 responses	 to	 climate	 change	
information.	 In	 S.	 C.	 Moser	 &	 L.	 Dilling	 (Eds.),	 Creating	 a	 climate	 for	 change:	 Communicating	
climate	change	and	facilitating	social	change	(pp.	64-80).	New	York:	Cambridge	University	Press.	
Moser,	S.C.,	&	Dilling,	L.	(2004).	Making	Climate	Hot:	Communicating	the	Urgency	and	Challenge	of	Global	
Climate	Change.	Environment,	46(10),	32-46.		
Nakajima,	T.,	&	Hamori,	S.	(2010).	Change	in	consumer	sensitivity	to	electricity	prices	in	response	to	retail	
deregulation:	 a	 panel	 empirical	 analysis	 of	 the	 residential	 demand	 for	 electricity	 in	 the	 United	
States.	Energy	policy,	38(5),	2470-2476.		
Nolan,	 J.	 M.	 (2010).	 “An	 Inconvenient	 Truth”	 increases	 knowledge,	 concern,	 and	 willingness	 to	 reduce	
greenhouse	gases.	Environment	and	Behavior,	42(5),	643-658.		
Nordlund,	A.	M.,	&	Garvill,	J.	(2002).	Value	structures	behind	proenvironmental	behavior.	Environment	and	
Behavior,	34(6),	740-756.		
Nordlund,	 A.	 M.,	 &	 Garvill,	 J.	 (2003).	 Effects	 of	 values,	 problem	 awareness,	 and	 personal	 norm	 on	
willingness	to	reduce	personal	car	use.	Journal	of	environmental	psychology,	23(4),	339-347.		
Norwegian	Ministry	of	the	Environment.	(1994).	Symposium	on	Sustainable	Consumption.	Oslo	Roundtable	
on	Sustainable	Production	and	Consumption.	http://www.iisd.ca/consume/oslo004.html	
Nye,	M.	,	Whitmarsh,	L.	,	&	Foxon,	T.	(2010).	Sociopsychological	perspectives	on	the	active	roles	of	domestic	
actors	in	transition	to	a	lower	carbon	electricity	economy.	Environment	and	Planning,	42(3),	697	–	
714.		
O’Keefe,	D.	J.	(1990).	Persuasion:	theory	and	research.	Michigan:	Sage	Publications.	
O’Keefe,	D.	J.	(2002).	Guilt	as	a	mechanism	of	persuasion.	In	J.	P.	Dillard	&	M.	Pfau	(Eds.),	The	persuasion	
handbook:	Developments	in	theory	and	practice	(pp.	329-344).	Thousand	Oaks,	CA:	Sage.	
Odyssee,	&	MURE.	(2011).	Energy	Efficiency	Policies	in	the	European	Union	-	Lessons	from	the	Odyssee-
Mure	Project:	Intelligent	Energy	Europe,	APEMS.	
OECD.	 (2012).	 Taxing	 Energy	 Use:	 A	 graphical	 analysis.	 http://www.oecd.org/tax/tax-
policy/taxingenergyuse.htm	
Ølander,	 C.	 F.,	 &	 Thøgersen,	 J.	 (1995).	 Understanding	 of	 consumer	 behaviour	 as	 a	 prerequisite	 for	
environmental	protection.	Journal	of	Consumer	Policy,	18(4),	345-385.		
OnePlanetLiving.	(n.d.).	Retrieved	08	of	July,	2013,	from	http://www.oneplanetliving.org/index.html.	
OSF.	 (2013).	 Energy	 consumption	 [e-publication].	 ISSN=1798-6869.	 Helsinki:	 Statistics	 Finland	 [referred:	
29.10.2013].	Access	method:	http://www.stat.fi/til/ekul/kas_en.html	
Osterhus,	T.	L.	(1997).	Pro-Social	Consumer	Influence	Strategies:	When	and	How	Do	They	Work?	Journal	of	
Marketing,	61(4),	16-29.		
Oxford	 University	 Press.	 (2013).	 Oxford	 English	 Dictionary	 (OED).	 Retrieved	 12	 of	 February,	 2013,	 from	
www.oed.com	
Patton,	M.	Q.	(2002).	Qualitative	Research	&	Evaluation	Methods:	Thousand	Oaks,	CA:	Sage	Publications.	
Peattie,	S.,	&	Peattie,	K.	(2003).	Ready	to	Fly	Solo?	Reducing	Social	Marketing's	Dependence	on	Commercial	
Theory.	Marketing	Theory,	3(3),	365-385.		
Petty,	R.	E.,	&	Cacioppo,	J.	T.	(1986).	The	elaboration	likelihood	model	of	persuasion.	In	L.	Berkowitz	(Ed.),	
Advances	in	experimental	social	psychology	(Vol.	19,	pp.	123-205).	New	York:	Academic	Press.	
Piaget,	J.	(1952).	The	Origins	of	Intelligence	in	Children.	New	York:	International	Universities	Press.
References	
	
220	
Piaget,	J.	(1969).	Mechanisms	of	perception.	(Translation	by	G.N.Seagrim)	New	York:	Basic	Books.	
Poortinga,	W.,	Pidgeon,	N.	F.,	&	Lorenzoni,	I.	(2006).	Public	Perceptions	of	Nuclear	Power,	Climate	Change	
and	 Energy	 Options	 in	 Britain:	 Summary	 Findings	 of	 a	 Survey	 Conducted	 during	 October	 and	
November	2005	Technical	Report	(Understanding	Risk	Working	Paper	06-02).	Norwich:	Centre	for	
Environmental	Risk.	
Poortinga,	W.,	Steg,	L.,	&	Vlek,	C.	(2004).	Values,	Environmental	Concern,	and	Environmental	Behavior	A	
Study	into	Household	Energy	Use.	Environment	and	behavior,	36(1),	70-93.		
Portuguese	 Government	 (2013).	 Council	 of	 Ministers	 Resolution	 No	 20/2013.	 The	 Portuguese	 Official	
Gazette	Series	1,	70.	
Poumanyvong,	P.,	&	Kaneko,	S.	(2010).	Does	urbanization	lead	to	less	energy	use	and	lower	CO2	emissions?	
A	cross-country	analysis.	Ecological	Economics,	70,	434–444.		
Powell,	R.	R.	(1997).	Basic	Research	Methods	for	Librarians:	Greenwood	Publishing	Group.	
Powell,	R.,	&	Single,	H.	(1996).	Focus	Groups.	International	Journal	of	Quality	in	Health	Care,	8(5),	499-504.		
Prendergrast,	 J.,	 Foley,	 B.,	 Menne,	 V.,	 &	 Isaac,	 A.	 K.	 (2008).	 Creatures	 of	 Habit:	 The	 Art	 of	 Behavioural	
Change.	London,	UK:	The	Social	Marketing	Foundation.	
Quercus.	(2008).	Projecto	EcoFamílias	–	Relatório	Final.		
Quitzau,	M-B.,	&	Røpke,	I.	(2008).	The	Construction	of	Normal	Expectations.	Consumption	Drivers	for	the	
Danish	Bathroom	Boom.	Journal	of	Industrial	Ecology,	12(2),	186	–	206.		
Randles,	S.	(2009).	Practice(s)	and	ratchet(s).	a	sociological	examination	of	frequent	flying.	In	P.	U.	Gössling	
(Ed.),	 Climate	 Change	 and	 Aviation:	 Issues,	 Challenges,	 and	 Solutions	 (pp.	 245-272).	 London:	
Earthscan	Ltd.	
Reynolds,	T.	W.,	Bostrom,	A.,	Read,	D.,	&	Morgan,	M.	G.	(2010).	Now	what	do	people	know	about	global	
climate	change?	Survey	studies	of	educated	laypeople.	Risk	Analysis,	30(10),	1520-1538.		
Roberts,	S.,	&	Baker,	W.	(2003).	Towards	effective	energy	information.	Improving	consumer	feedback	on	
energy	consumption.	A	report	to	OFGEM.	http://www.cse.org.uk/pdf/pub1014.pdf	
Rohan,	M.	J.	(2000).	A	rose	by	any	name?	The	values	construct.	Personality	and	social	psychology	review,	
4(3),	255-277.		
Rossini,	Giuliana,	2009.	“Hydro	One:	In	Home	Real	Time	Display:	Customer	Feedback	from	a	30,000	Unit	
Deployment”.	Home	Energy	Displays	Conference,	Orlando,	2	April	2009	
Rotter,	J.	B.	(1954).	Social	learning	and	clinical	psychology,	Englewood	Cliffs:	Prentice-Hall.	
Royal	Society	of	London,	&	U.S.	National	Academy	of	Sciences.	(1997).	Towards	Sustainable	Consumption.	
Population	and	Development	Review,	23(3),	683-686.		
Rudestam,	 Kjell	 Erik	 &	 Newton,	 Rae	 R.	 (2001).	 Surviving	 Your	 Dissertation:	 A	 Comprehensive	 Guide	 to	
Content	and	Process,	London:	SAGE	Publications.	
Schiffman,	Leon,	&	Kanuk,	Leslie.	(1999).	Consumer	Behavior:	Prentice	Hall.	
Schipper,	L.,	&	Grubb,	M.	(2000).	On	the	rebound?	Feedback	between	energy	intensities	and	energy	uses	in	
IEA	countries.	Energy	Policy,	28(6-7),	367–388.		
Schultz,	P.	W.	(2002).	Knowledge,	Information,	and	Household	Recycling:	Examining	the	Knowledge-Deficit	
Model	of	Behavior	Change.	In	T.	Dietz	&	P.	C.	Stern	(Eds.),	New	tools	for	environmental	protection:	
education,	 information,	 and	 voluntary	 measures	 (1st	 ed.,	 pp.	 67-82).	 Washington	 DC:	 National	
Academies	Press.
References	
	
221	
Schultz,	P.	W.,	Gouveia,	V.	V.,	Cameron,	L.	D.,	Tankha,	G.,	Schmuck,	P.,	&	Franěk,	M.	(2005).	Values	and	their	
relationship	 to	 environmental	 concern	 and	 conservation	 behavior.	 Journal	 of	 cross-cultural	
psychology,	36(4),	457-475.		
Schultz,	 P.	 W.,	 Nola,	 J.	 M.,	 Cialdini,	 R.	 B.,	 Goldstein,	 N.	 J.,	 &	 Griskevicius,	 V.	 (2007).	 The	 Constructive,	
Destructive,	and	Reconstructive	Power	of	Social	Norms.	Psychological	Science,	18(5),	429-434.		
Schultz,	 P.	 W.,	 Oskamp,	 S.,	 &	 Mainieri,	 T.	 (1995).	 Who	 recycles	 and	 when?	 A	 review	 of	 personal	 and	
situational	factors.	Journal	of	Environmental	Psychology,	15(2),	105-121.		
Schwartz,	 B.	 (in	 Hastings,	 G.	 (2008).	 Social	 Marketing:	 Why	 should	 the	 devil	 have	 all	 the	 best	 tunes?	
Butterworth	Heinemann.	
Schwartz,	S.	H.	(1970).	Elicitation	of	moral	obligation	and	self-sacrificing	behavior.	Journal	of	Personality	and	
Social	Psychology,	15,	283-293.		
Schwartz,	S.	H.	(1977).	Normative	influences	on	altruism.	In	L.	Berkowitz	(Ed.),	Advances	in	experimental	
social	psychology	(Vol.	10,	pp.	221-279).	San	Diego,	CA:	Academic	Press.	
Schwartz,	S.	H.	(1992).	Universals	in	the	content	and	structure	of	values:	Theory	and	empirical	tests	in	20	
countries.	In	M.	Zanna	(Ed.),	Advances	in	experimental	social	psychology	(Vol.	25,	pp.	1–65).	New	
York:	Academic	Press.	
Schwitzgebel,	E.	(2010).	Acting	Contrary	to	Our	Professed	Beliefs,	or	The	Gulf	Between	Occurrent	Judgment	
and	Dispositional	Belief.	Pacific	Philosophical	Quarterly,	91,	531-553.		
Scottish	Government.	(2010).	Summary	of	differences	in	UK	Fuel	Poverty	methodologies.	
Sedgwick,	Peter,	&	Edgar,	Andrew.	(1999).	Key	Concepts	in	Cultural	Theory.	London,	UK:	Routledge.	
SEI.	(2003).	A	Review	of	Fuel	Poverty	and	Low	Income	Housing	(pp.	72).	Ireland:	Sustainable	Energy	Ireland	
(SEI).	
Sherif,	 C.	 W.,	 Sherif,	 M.,	 &	 Nebergall,	 R.	 E.	 (1965).	 Attitudes	 and	 attitude	 change:	 The	 social	 judgment-
involvement	approach.	Philadelphia:	W.	B.	Saunders.	
Sherif,	M.,	&	Hovland,	C.	I.	(1961).	Social	judgment:	Assimilation	and	contrast	effects	in	communication	and	
attitude	change.	New	Haven,	CT:	Yale	University	Press.	
Shome,	 D.,	 &	 Marx,	 S.	 (2009).	 The	 psychology	 of	 climate	 change	 communication:	 a	 guide	 for	 scientists,	
journalists,	 educators,	 political	 aides,	 and	 the	 interested	 public	 (A.	 Cimino	 &	 Leapfrog	
Communications	 Eds.).	 New	 York:	 The	 Trustees	 of	 Columbia	 University,	 Centre	 for	 Research	 on	
Environmental	Decisions.	
Shove,	 E.	 (2003).	 Converging	 conventions	 of	 comfort,	 cleanliness	 and	 convenience.	 Journal	 of	 Consumer	
Policy,	26(4),	395-418.		
Shove,	E.	(2004).	Efficiency	and	Consumption:	Technology	and	Practice.	Energy	&	Environment,	15(6),	1053-
1065.		
Shove,	 E.	 (2005).	 Consumption	 -	 Perspectives	 from	 ecological	 economics.	 In	 Ropke,	 I.	 &	 Reisch,	 L.	 (Ed.).	
Cheltenham:	Elgar,	p.	111-132	22	p.	
Shove,	E.	(2006).	Efficiency	and	consumption:	technology	and	practice.	In	T.	Jackson	(Ed.),	The	Earthscan	
Reader	in	Sustainable	Consumption.	London,	Sterling	VA:	Earthscan.	
Shove,	E.	(2009).	Habits	and	their	creatures	(pp.	3):	Department	of	Sociology,	Lancaster	University.	
Shove,	E.,	&	Southerton,	D.		(2000).	Defrosting	the	Freezer:	From	Novelty	to	Convenience	A	Narrative	of	
Normalization.	Journal	of	Material	Culture,	5(3),	301-319.
References	
	
222	
Shove,	E.;	Chappells,	H.;	Lutzenhiser,	L.,	&	Hackett,	B.	(2008).	Comfort	in	a	lower	carbon	society.	Building	
Research	&	Information,	36(4),	307-311.	
SILC.	 (2007).	 Module:	 Housing	 conditions.	
http://epp.eurostat.ec.europa.eu/portal/page/portal/income_social_inclusion_living_conditions/d
ata/ad_hoc_modules	
Simons,	 H.	 W.	 (1976).	 Persuasion:	 Understanding,	 Practice,	 and	 Analysis.	 London,	 UK:	 Addison-Wesley	
Publishing	Company.	
Skinner,	B.	F.	(1971).	Beyond	freedom	and	dignity.	New	York:	Alfred	A.	Knopf.	
Slovic,	P.	(2000).	The	perception	of	risk.	London:	Earthscan.	
Slovic,	P.,	Finucane,	M.	L.,	Peters,	E.,	&	MacGregor,	D.	G.	(2004).	Risk	as	analysis	and	risk	as	feelings:	Some	
thoughts	about	affect,	reason,	risk,	and	rationality.	Risk	analysis,	24(2),	311-322.		
Smith,	A.	(1776).	An	Inquiry	into	the	Nature	and	Causes	of	the	Wealth	of	Nations	(E.	Cannan	Ed.):	University	
Of	Chicago	Press.	
Sorrell,	S.	(2007).	The	Rebound	Effect:	an	assessment	of	the	evidence	for	economy-wide	energy	savings	
from	improved	energy	efficiency.	UK:	The	UK	Energy	Research	Centre	(UKERC).	
Southerton,	 D.,	 McMeekin,	 A.,	 &	 Evans,	 D.	 (2011).	 International	 Review	 of	 Behaviour	 Change	 Initiatives			
Retrieved	from	www.scotland.gov.uk/socialresearch		
Spaargaren,	 G.,	 &	 van	 Vliet,	 B.	 (2000).	 Lifestyle,	 Consumption	 and	 the	 Environment:	 the	 ecological	
modernisation	of	domestic	consumption.	Society	and	Natural	Resources,	9,	50-76.		
Staats,	 H.,	 Harland,	 P.,	 &	 Wilke,	 H.	 A.	 (2004).	 Effecting	 durable	 change	 a	 team	 approach	 to	 improve	
environmental	behavior	in	the	household.	Environment	and	Behavior,	36(3),	341-367.		
Staats,	 H.	 J.,	 Wit,	 A.	 P.,	 &	 Midden,	 C.	 Y.	 H.	 (1996).	 Communicating	 the	 greenhouse	 effect	 to	 the	 public:	
Evaluation	of	a	mass	media	campaign	from	a	social	dilemma	perspective.	Journal	of	Environmental	
Management,	45,	189–203.		
Staats,	H.,	Leeuwen,	E.,	&	Wit,	A.	(2000).	A	longitudinal	study	of	informational	interventions	to	save	energy	
in	an	office	building.	Journal	of	Applied	Behavior	Analysis,	33(1),	101-104.		
Stake,	R.	(1995).	The	art	of	case	study	research.	Thousand	Oaks,	CA:	Sage	Publications.	
Steg,	L.	(2003).	Can	public	transport	compete	with	the	private	car.	IATSS	Research,	27(2),	27–35.		
Steg,	 L.,	 Dreijerink,	 L.,	 &	 Abrahamse,	 W.	 .	 (2006).	 Acceptability	 of	 Energy	 Policies.	 Environment	 and	
Behavior,	38,	92-111.		
Stern,	N.	(2007).	The	Economics	of	Climate	Change:	The	Stern	Review:	Cambridge	University	Press.	
Stern,	 P.	 C.	 (1992).	 What	 psychology	 knows	 about	 energy	 conservation.	 American	 Psychologist,	 47(10),	
1224-1232.		
Stern,	P.	C.	(1997).	Toward	a	working	definition	of	consumption	for	environmental	research	and	policy.	In	P.	
C.	Stern,	T.	Dietz,	V.	R.	Ruttan,	R.	H.	Socolow,	&	J.	L.	Sweeney	(Eds.),	Environmentally	significant	
consumption:	Research	directions	(pp.	12–35).	Washington,	DC:	National	Academy	Press,	1997.	
Stern,	P.	C.	(1999).	Information,	incentives,	and	proenvironmental	consumer	behavior.	Journal	of	Consumer	
Policy,	22,	461–478.		
Stern,	 P.	 C.	 (2000).	 Toward	 a	 Coherent	 Theory	 of	 Environmentally	 Significant	 Behavior.	 Journal	 of	 Social	
Issues,	56(3),	407–424.
References	
	
223	
Stern,	P.	C.,	Dietz,	T.,	Kalof,	L.,	&	Guagnano,	G.	A.	(1995).	Values,	beliefs,	and	pro-environmental	action:	
attitude	 formation	 toward	 emergent	 attitude	 objects.	 Journal	 of	 Applied	 Social	 Psychology,	 25,	
1611-1636.		
Stevensen,	F,	&	Rijal,	H.	B.	(2010).	Developing	occupancy	feedback	from	a	prototype	to	improve	housing	
production.	Building	Research	&	Information,	35	(5),	549-563.	
Streimikiene,	D.	(2012).	The	impact	of	intervention	measures	on	household	energy	conservation	and	the	
GHG	emission	reduction	in	Lithuania.	Intellectual	Economics,	6(1	(13)),	713-729.		
Streimikiene,	D.,	&	Ciegis,	R.	(2010).	The	Changes	of	Life	Style:	Significant	Contribution	to	GHG	emission	
Reduction	 Efforts.	 In	 W.	 L.	 Filho	 (Ed.),	 Universities	 for	 Climate	 Change	 (pp.	 280-299).	 Berlin:	
Springer-Verlag.	
Strengers,	 Y.	 (2008).	 Comfort	 expectations:	 the	 impact	 of	 demand-management	 strategies	 in	 Australia,	
Building	Research	&	Information,	36	(4),	381-391.	
Tabara,	 D.,	 Darier,	 E.,	 Gerger,	 A.,	 Kasemir,	 B.,	 Schule,	 R.,	 1999.	 Knowledge	 for	 sustainability:	 reflexive	
learning	 and	 mass	 communication	 on	 Global	 Environmental	 Change.	 Paper	 based	 on	 research	
carried	out	under	the	ULYSSES	Project,	financed	by	DG	XII	of	the	European	Commission.	
Tashakkori,	A.,	&	Teddlie,	C.	(2010).	Handbook	of	mixed	methods	in	social	&	behavioral	research	(pp.	189-
208).	London:	Sage	Publications.	
Thaler,	R.	H.	(1981).	Some	empirical	evidence	on	dynamic	inconsistency.	Economics	Letters,	8(3),	201-207.		
Thaler,	R.	H.,	&	Sunstein,	C.	R.	(2008).	Nudge:	Improving	decisions	about	health,	wealth,	and	happiness:	Yale	
University	Press.	
The	Royal	Society.	(2012).	People	and	the	planet,	summary	and	recommendations.	London,	UK:	The	Royal	
Society	Science	Policy	Centre,	Excellence	in	Science.	
The	University	of	York.	(n.d.).	EU	Fuel	Poverty	Network.	http://fuelpoverty.eu/	
Thøgersen,	J.	(2005).	How	may	consumer	policy	empower	consumers	for	sustainable	lifestyles.	Journal	of	
Consumer	Policy,	18,	143-178.		
Thøgersen,	 J.,	 &	 Møller,	 B.	 (2008).	 Breaking	 car	 use	 habits:	 The	 effectiveness	 of	 a	 free	 one-month	
travelcard.	Transportation,	35(3),	329-345.		
Thøgersen,	 John.	 (2004).	 A	 cognitive	 dissonance	 interpretation	 of	 consistencies	 and	 inconsistencies	 in	
environmentally	responsible	behavior.	Journal	of	Environmental	Psychology,	24(1),	93-103.		
Thøgersen,	 John,	 &	 Ølander,	 Carl	 Folke.	 (2002).	 Human	 values	 and	 the	 emergence	 of	 a	 sustainable	
consumption	pattern:	A	panel	study.	Journal	of	Economic	Psychology,	23(5),	605-630.		
Thomas,	C.,	&	Sharp,	V.	(2013).	Understanding	the	normalisation	of	recycling	behaviour	and	its	implications	
for	 other	 pro-environmental	 behaviours:	 a	 review	 of	 social	 norms	 and	 recycling.	 Resources,	
Conservation	and	Recycling,	79,	11–20.		
Throne-Holst,	H.,	Strandbakken,	P.,	&	Stø,	E.	(2008).	Identification	of	households'	barriers	to	energy	saving	
solutions.	Management	of	Environmental	Quality:	An	International	Journal,	19(1),	54	-	66.		
Tobler,	C.,	Visschers,	V.	H.,	&	Siegrist,	M.	.	(2012).	Addressing	climate	change:	Determinants	of	consumers'	
willingness	to	act	and	to	support	policy	measures.	Journal	of	Environmental	Psychology,	32(3),	197-
207.		
Townsend,	P.	(1979).	Poverty	in	the	United	Kingdom.	London,	UK:	Allen	Lane	and	Penguin	Books.	
Triandis,	H.	(1977).	Interpersonal	Behaviour.	Monterey,	CA:	Brooks/Cole.
References	
	
224	
Tversky,	 A.,	 &	 Kahneman,	 D.	 (1991).	 Loss	 aversion	 in	 riskless	 choice:	 a	 reference	 dependent	 model.	
Quarterly	journal	of	economics,	106,	1039-1061.		
U.S.	Census	Bureau.	(2011).	International	Data	Base.	In	U.	S.	D.	o.	C.	United	States	Census	Bureau	(Ed.).	
UK	 Government.	 (2013).	 Fuel	 Poverty	 Statistics.	
https://www.gov.uk/government/organisations/department-of-energy-climate-
change/series/fuel-poverty-statistics	
UN.	 (1987).	 Report	 of	 the	 World	 Commission	 on	 Environment	 and	 Development:	 Our	 Common	 Future.	
Transmitted	 to	 the	 General	 Assembly	 as	 an	 Annex	 to	 document	 A/42/427	 -	 Development	 and	
International	Co-operation:	Environment.	http://www.un-documents.net/wced-ocf.htm	
UN.	(1992).	Agenda	21	Rio	declaration			Retrieved	from	http://www.un-documents.net/agenda21.htm		
UN.	(2007).	World	Population	Prospects,	The	2006	Revision,	Highlights.	New	York:	Department	of	Economic	
and	Social	Affairs,	Population	Division.	
UN.	(2011).	File	1:	Total	population	(both	sexes	combined)	by	major	area,	region	and	country,	annually	for	
1950-2100	 (thousands):	 United	 Nations	 (UN),	 Department	 of	 Economic	 and	 Social	 Affairs,	
Population	Division.	
Upham,	 P.,	 Whitmarsh,	 L.,	 Poortinga,	 W.,	 Purdam,	 K.,	 Darnton,	 A.,	 McLachlan,	 C.,	 &	 Devine-Wright,	 P.	
(2009).	 Public	 Attitudes	 to	 Environmental	 Change:	 a	 selective	 review	 of	 theory	 and	 practice.	
Manchester,	UK:	ESRC/LWEC.	
Uusitalo,	L.	(1990).	Are	Environment	Attitude	and	Behaviour	Inconsistent?	Finding	from	a	Finnish	Study.	
Scandinavian	Political	Studies,	13(2),	211-226.		
van	 der	 Pligt,	 J.	 (1985).	 Energy	 conservation:	 two	 easy	 ways	 out.	 Journal	 of	 Applied	 Social	 Psychology	
Bulletin,	15(1),	3-15.		
Vandenbergh,	M.,	Barkenbus,	J.,	&	Gilligan,	J.	(2008).	Individual	carbon	emissions:	The	low-hanging	fruit.	
UCLA	Law	Review,	55,	8-36.		
Verplanken,	 B.,	 &	 Faes,	 S.	 (1999).	 Good	 intentions,	 bad	 habits,	 and	 effects	 of	 forming	 implementation	
intentions	on	healthy	eating.	European	Journal	of	Social	Psychology,	29(5-6),	591-604.		
Verplanken,	B.,	&	Holland,	R.	(2002).	Motivated	decision	making:	Effects	of	activation	and	self-centrality	of	
values	on	choices	and	behavior.	Journal	of	Personality	and	Social	Psychology,	82,	434-447.		
Vygotsky,	 L	 S	 (1978)	 “Mind	 and	 Society:	 the	 Development	 of	 Higher	 Psychological	 Processes”,	 Harvard	
University	Press,	Cambridge.	MA.	
Wackernagel,	M.,	Schulz,	B.,	Deumling,	D.,	Callejas	Linares,	A.,	Jenkins,	M.,	Kapos,	V.,	Randers,	J.	(2002).	
Tracking	the	ecological	overshoot	of	the	human	economy.	Proceedings	of	the	National	Academy	of	
Sciences	of	the	United	States	of	America,	99(14),	9266-9271.		
Weaver,	K.,	&	Olson,	J.	K.	(2006).	Understanding	paradigms	used	for	nursing	research.	Journal	of	Advanced	
Nursing,	53(4),	459-469	
Weber,	 E.	 U.	 (1997).	 Perception	 and	 expectation	 of	 climate	 change:	 Precondition	 for	 economic	 and	
technological	adaptation.	In	M.	Bazerman,	 D.	Messick,	A.	Tenbrunsel	&	K.	Wade-Benzoni	(Eds.),	
Psychological	 and	 Ethical	 Perspectives	 to	 Environmental	 and	 Ethical	 Issues	 in	 Management	 (pp.	
314-341).	San	Francisco:	Jossey-Bass.	
Weber,	 E.	 U.	 (2006).	 Evidence-based	 and	 description-based	 perceptions	 of	 long-term	 risk:	 Why	 global	
warming	does	not	scare	us	(yet).	Climatic	Change,	77,	103-120.		
Weinreich,	N.	K.	(1999).	Hands	on	social	marketing:	A	step	by	step	guide.	Thousand	Oaks,	CA:	Sage.
References	
	
225	
Whitmarsh,	 L.	 E.	 (2009).	 Social	 and	 psychological	 drivers	 of	 energy	 consumption	 behaviour	 and	 energy	
transitions.	In	S.	Dietz,	J.	Michie	&	C.	Oughton	(Eds.),	Political	Economy	of	the	Environment:	An	
Interdisciplinary	Approach	(pp.	213-228):	Taylor	&	Francis.	
Whitmarsh,	 L.	 E.,	 Turnpenny,	 J.,	 &	 Nykvist,	 B.	 (2009).	 Beyond	 the	 regime:	 can	 Integrated	 Sustainability	
Assessment	 address	 the	 barriers	 to	 effective	 sustainable	 passenger	 mobility	 policy?	 Journal	 of	
Environmental	Planning	and	Management,	52(8),	973-991.		
Wilhite,	H.,	&	Lutzenhiser,	L.	(1999).	Social	Loading	and	Sustainable	Consumption.	In	E.	J.	Arnould	&	L.	M.	
Scott	(Eds.),	NA	-	Advances	in	Consumer	Research	(Vol.	26,	pp.	281-287).	Provo,	UT:	Association	for	
Consumer	Research.	
Wilhite,	H.	&	Richard,	L.	(1992).	"The	Person	Behind	the	Meter:	An	Ethnographic	Analysis	of	Residential	
Energy	Consumption	in	Oslo,	Norway."	Proceedings	from	the	ACEEE	1992	Summer	Study	on	Energy	
Efficiency	in	Buildings	10:177-186.	Washington,	D.	C.:	ACEEE	Press.	
Wilkinson,	D.,	&	Birmingham,	P.	(2003).	Using	Research	Instruments:	a	guide	for	researchers.	London,	UK:	
Routledge.	
Williamson,	T.;	Soebarto,	V.	&	Radford,	A.	(2010).	Comfort	and	energy	use	in	five	Australian	award-winning	
houses:	regulated,	measured	and	perceived,	Building	Research	&	Information,	38(5),	509-529.	
Winett,	 R.	 A.,	 &	 Kagel,	 J.	 H.	 (1984).	 Effects	 of	 information	 presentation	 format	 on	 resource	 use	 in	 field	
studies.	Journal	of	Consumer	Research,	11,	655–667.		
Winett,	R.	A.,	Leckliter,	I.	N.,	Chinn,	D.	E.,	Stahl,	B.,	&	Love,	S.	Q.	(1985).	Effects	of	television	modeling	on	
residential	energy	conservation.	Journal	of	Applied	Behavior	Analysis,	18,	33–44.		
Winter,	D.	D.	N.	,	&	Koger,	S.	M.	(2004).	The	Psychology	of	Environmental	Problems:	Lawrence	Erlbaum.	
Wright,	A.	(2008).	What	is	the	relationship	between	built	form	and	energy	use	in	dwellings?	Energy	Policy,	
36(12),	4544-4547.		
WHO.	 (2012).	 Environmental	 health	 inequalities	 in	 Europe.	 Copenhagen,	 Denmark:	 World	 Health	
Organization	(WHO).	
WWF.	(2008).	Living	Planet	report	2008:	World	Wide	Fund	for	Nature	(WWF).	
WWF.	(2012).	Living	Planet	report	2012	-	Biodiversity,	biocapacity	and	better	choices:	World	Wide	Fund	for	
Nature	(WWF).
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Appendices	
Appendix	I:	Energyprofiler	survey	questionnaire
Appendices	
	
227
Appendices	
	
228
Appendices	
	
229
Appendices	
	
230
Appendices	
	
231
Appendices	
	
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Appendices	
	
234	
Appendix	II:	Reduced	version	-	FG	questionnaire	before	discussion
Appendices	
	
235	
Appendix	III:	Consumer	interview	roadmap	
1. How	easy	or	difficult	do	you	find	to	reduce	the	amount	of	energy	you	use	at	home	on	a	day	to	day	
base?	
a. Follow	up	question:	what	are	the	reasons	for	easiness	or	difficultness?	
b. Follow	up	question:	if	you	would	need	to	chose	one	reason	from	all	the	above	for	easiness	
or	difficultness	which	one	would	it	be?	
c. Back	up	information:	list	of	barriers	from	FG:	
i. Comfort	
ii. Habits	
iii. Willingness/Laziness/resistance	to	change	
iv. Self-indulgence	
v. Environment/future	
vi. Initial	investment/RoI	
vii. Information	
viii. Actions	already	taken	
ix. Economical	conditions	
x. Social	norms,	social	dilemma	and	hypocrisy	
	
2. What	does	comfort	mean	to	you	at	home?	How	does	it	affect	your	day	to	day	use	of	energy?	Can	
you	provide	some	examples?		
a. Prompt	for	thermal	comfort	
b. Prompt	for	showering	habits	
c. Prompt	for	lighting	practices	
d. Prompt	for	having	the	TV	on	even	if	not	watching		
e. Prompt	for	leaving	stand-by	on	
f. Prompt	for	using	appliances	such	as	washing	machines	at	any	point	of	the	day	
g. Prompt	for	leaving	fridge	open	
	
3. Can	you	describe	your	expectations	of	a	minimum	level	of	comfort	at	home?	
	
4. If	you	had	to	chose	between	spending	less	on	energy	and	maintaining	your	comfort	level,	what	
would	you	chose?		
a. At	which	point	would	your	priorities	change?		
b. What	could	trigger	change?	
c. Have	you	ever	been	at	a	situation	were	you	needed	to	reduce	your	comfort	level?	Can	you	
describe	the	circumstances?
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236	
5. Some	 people	 have	 been	 referring	 to	 the	 fact	 that	 changing	 some	 of	 their	 behaviours	 might	 be	
quite	inconvenient/you	have	mentioned	the	fact	that	changing	some	of	those	behaviours	would	be	
quite	 inconvenient	 to	 you.	 Is	 comfort	 and	 convenience	 the	 same	 to	 you?	 What	 are	 the	
similarities/differences	between	the	two	of	them?	
a. Prompt	for	standby	
b. Prompt	for	off	peak	tariffs	
c. Prompt	for	leaving	the	door	of	the	fridge	opne/open	frequently	
d. Prompt	for	cooking	with	lids	on	
	
6. Which	actions	could	you	take	in	order	to	reduce	your	energy	bill	without	reducing	your	comfort	
level?	(Write	in	a	paper)	
a. Follow	up:	can	you	please	order	the	actions	you	just	mentioned,	starting	with	the	one	you	
would	do	first	to	the	one	you	would	do	the	last	(use	the	paper	from	above)		
b. Follow	up	question:	Can	you	develop	on	the	reasoning	of	the	ordering?		
	
7. How	do	you	consider	your	energy	use	level	at	home?	High,	normal,	average,	low	or	conditioned?	
a. Can	you	explain	the	reasons	for	locating	yourself	as	XXX?		
b. What	is	for	you	a	‘normal’	energy	use	level?	
c. 	How	would	you	describe	it?	
d. What	about	your	family	and	friends?	How	do	you	perceive	their	energy	use	to	be?	
e. Where	do	you	locate	yourself	within	this	graph?
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237	
f. How	do	you	see	yourself	in	10	years	within	the	graph?	Why	do	you	think	that	is?	
Imagine	you	need	to	reduce	your	energy	consumption	by	half?	Which	of	your	basic	needs	you	would	want	
to	maintain?	What	could	be	considered	a	luxury	under	those	circumstances?
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Appendix	IV:	Practitioner	interview	roadmap	
1. How	easy	or	difficult	do	you	think	it	is	for	people	to	reduce	their	energy	use	at	home	?	
a. How	do	you	understand	the	easiness	to	change	one	time	investment	decisions?		
b. How	do	you	understand	the	easiness	to	change	daily	habitual	behaviours?		
2. Which	barriers	to	change	do	people	face	in	reducing	their	energy	use	with	regards	to	changing	
their	daily	habitual	behaviours?	
a. Backup	information:	
i. Lack	of	information	
ii. Lack	of	financial	resources	
iii. Resistance	to	change	
iv. Ingrained	habits	
v. Lack	of	motivation	
vi. Lack	of	environmental	concerns	
vii. Lack	 of	 connection	 between	 their	 individual	 energy	 use	 to	 the	 global	
consumption	
viii. Locked	to	building	infrastructure	
ix. Limited	by	other	family	members	
x. Unwillingness	to	reduce	comfort	level	
xi. Convenience	of	current	behaviours	
3. From	the	barriers	you	mentioned,	which	do	you	identify	as	important	once	designing	interventions	
and	why?	
a. Can	you	recall	an	example	when	that	was	done?		
b. Have	those	interventions	been	effective?	
c. How	do	you	know	that?	
d. Has	 your	 organization	 focused	 their	 interventions	 on	 any	 of	 those	 barriers	 you	 just	
mentioned	as	important?	If	not,	what	could	be	the	reason	for	such?	If	yes,	how	successful	
have	they	been?	
e. How	do	you	perceive	that	people	receive	and	enrol	on	initiatives	to	promote	less	energy	
intensive	lifestyles	
4. You	have	been	mentioning/people	have	been	mentioning	that	maintaining	comfort	level	is	quite	
important	for	them.	What	do	you	think	people	mean	by	comfort?	
a. What	is	your	understanding	of	the	role	of	comfort	as	a	barrier	to	change	individual	energy	
use?	
b. Has	your	organization	ever	tried	to	tackle	the	existing	expectation	for	comfort	within	their	
interventions?	
c. How	do	you	think	comfort	should	be	included	within	future	interventions?	
d. Do	 you	 think	 it	 would	 be	 feasible	 to	 promote	 an	 adaptation	 of	 the	 level	 of	 individual	
comfort?
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239	
e. How	would	you	communicate	the	need	to	reduce	comfort	in	a	world	that	might	run	out	of	
energy,	how	would	you	disrupt	the	flow	of	current	messages	and	set	a	different	agenda?		
5. You	have	been	mentioning/people	have	been	mentioning	that	changing	their	daily	behaviours	is	
inconvenient.	What	do	you	think	people	mean	by	convenience?	
a. What	is	your	understanding	of	the	role	of	convenience	as	a	barrier	to	change	individual	
energy	use?	
b. Has	your	organization	ever	tried	to	tackle	the	existing	expectation	for	convenience	within	
their	interventions?	
c. How	do	you	think	convenience	should	be	included	within	future	interventions?	
d. Do	you	think	it	would	be	feasible	to	promote	an	adaptation	of	the	level	of	convenience	of	
current	behaviours?	
6. In	your	opinion,	what	does	‘normal’	energy	consumption	means	to	individual	users	or	households?	
KWh,	cost	or	services?	
a. How	do	you	consider	individual	users	are	influenced	by	what	they	see	as	normal?		
b. How	could	one	influence	this	idea	of	‘normal’	consumption?	
c. Has	your	organization	ever	tried	to	tackle	the	existing	norms	within	their	interventions?	
d. How	do	you	think	norms	should	be	included	within	future	interventions?	
e. How	would	you	communicate	the	need	to	change	norms?	
f. Do	you	believe	norms	could	be	changed	through	a	carrot	and	stick	approach?		
g. Do	you	think	it	would	be	feasible	to	promote	an	adaptation	of	norms?
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240	
Appendix	 V:	 List	 of	 answers	 for	 Question	 6	 of	 EP	 survey	 questionnaire	
regarding	energy	saving	reported	behaviours
Appendices	
	
241	
Appendix	VI:	–	List	of	answers	for	Question	15	of	EP	survey	questionnaire	
regarding	energy	saving	reported	behaviours
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242	
Appendix	VII:	Variables	defined	during	energyprofiler	study
Appendices	
	
243	
Appendix	VIII:	–	List	of	answers	for	question	Q16	of	EP	survey	questionnaire	
(reported	barriers	and	constraints)	
	
	 	
0,0% 10,0% 20,0% 30,0% 40,0% 50,0% 60,0%
Already	do	what	I	can
I	save	enough	already/I	save	too	much	already
I	would	like	to	do	more,	but	don’t	know	how
It	would	reduce	my	comfort
I	don’t	have	time	to	do	more/I’m	too	busy
I	don’t	want	 to	know/it	doesn’t	concern	me
It’s	not	useful/it’s	not	necessary
It	would	be	very	expensive
The	greatest	polluter	is	the	industry
It	wouldn’t	make	any	difference
I	don’t	see	any	reduction	in	the	bill
Alone	it	wouldn’t	make	any	difference/I	do	it	…
The	future	will	come	up	with	solutions
Electricity/gas	is	cheap	/	I	pay	very	little
50,3%
22,1%
16,9%
10,6%
8,2%
3,9%
2,3%
1,7%
1,4%
1,4%
0,9%
0,9%
0,8%
0,2%
Reported	barriers	to	save	energy	(in	%)
Appendices	
	
244	
Appendix	IX:	–	List	of	identified	barriers	during	the	FG
Appendices	
	
245	
Appendix	X:	–	Sample	distribution	with	regard	to	region,	gender,	age	groups	
and	rural/urban	area	
	
		
		
		
Male	 Female	 		
16-25	
years	
25-45	
years	
>45	
years	
16-25	
years	
25-45	
years	
>45	
years	 Total	
North	
URBAN	 14	 15	 14	 14	 14	 14	 85	 170	
(16.7%)	RURAL	 14	 14	 14	 14	 15	 14	 85	
Centre	
URBAN	 14	 14	 14	 14	 15	 15	 86	 172	
(16.9%)	RURAL	 14	 14	 14	 15	 14	 15	 86	
Lisboa	
URBAN	 12	 16	 12	 14	 16	 9	 79	 164	
(16.1%)	RURAL	 14	 14	 14	 14	 15	 14	 85	
Alentejo	
URBAN	 14	 14	 14	 14	 14	 14	 84	 170	
(16.7%)	RURAL	 14	 14	 14	 15	 14	 15	 86	
Algarve	
URBAN	 14	 14	 14	 14	 14	 14	 84	 170	
(16.7%)	RURAL	 15	 15	 14	 14	 14	 14	 86	
Islands	
URBAN	 14	 14	 14	 14	 14	 15	 85	 173	
(17%)	RURAL	 14	 15	 14	 15	 15	 15	 88	
	
		 167	 173	 166	 171	 174	 168	 1.019

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The role of behaviour in the transition to more energy efficient use at home – Lessons from Portugal

  • 2. I Abstract This study investigated domestic energy use behaviours in Portugal and ways of reducing energy use. This is important because current energy use in the developed world is considered to be unsustainable. Intervention strategies could play an important role to reduce energy use. While some previous research has demonstrated that certain intervention strategies did, or did not, produce changes in behaviour, they mostly could not sufficiently explain the underlying and impacting determinants, or how change came about and led to the desired adoption, whether short or long-term, of more energy efficient behaviours. This study therefore aims to explore how the adoption of more energy efficient behaviours at home could be encouraged. With this the research has the objective to better understand the different determinants of energy use at home, the underlying motivations, barriers and potential intervention strategies. To achieve this the study uses an exploratory and iterative multi-method approach consisting of survey questionnaires, followed by qualitative research through focus groups targeted at energy users at home, and also individual in-depth interviews with energy conservation intervention practitioners. The findings of this research show that if the rate of adoption of more energy efficient behaviours is to increase, then interventions that are focusing on providing information or financial incentives, are unlikely to work for a large proportion of energy users. Instead, the adoption of more energy efficient behaviours at home is seen to depend on the ability of intervention strategies to challenge existing norms, thus creating new understandings, expectations and utilization of energy services that could manifest in the adoption of more energy efficient behaviours. With this findings also suggest that community-based initiatives might be an adequate means to challenge social norms and to bring about change.
  • 3. II Declaration This is to certify that: The thesis comprises only my original work towards the PhD except where indicated, due acknowledgements have been made in the text to all other material used, the thesis is less than 100,000 words in length, inclusive of all footnotes, bibliographies and appendices. _____________ Ana Faria December 2014
  • 4. III Acknowledgments First and foremost I would like to thank my partner in life Andreas for challenging me at first and supporting me afterwards from the very beginning of my journey until today. I would like to extend my gratitude to my parents who on their singular way have always supported me throughout these years. My PhD journey started out of a passion for the area I work in and the vast number of on-going open questions to explore. Having said that, I would like to thank the Open University and Professor Joaquim Borges Gouveia, President of the board of Energaia, for the opportunity provided by granting me the right and flexibility to carry out my PhD work within a joint enterprise / academic partnership. I would like to extend my acknowledgement to my current and former work colleagues, in particular to the 2 Js (João and José) for their support, and for all the fruitful talks and companionships. With regards to the actual body of this work I’d like to express my gratitude to the Entidade Reguladora do Sector Energético (ERSE) for selecting the Energyprofiler project for funding, which supported my research at its initial stage. It was within the scope of this project that I had the pleasure to work together with a highly skilled and motivated team and to learn how to become a researcher through practice. This collaboration brought up a number of opportunities that would have been difficult to realize otherwise. The Energyprofiler project provided me with the opportunity to explore the topic on a larger, national scale that otherwise would have been difficult to achieve. The project also allowed me to work together with Dalila Antunes and Rui Gaspar, who were that patient to walk me through the initial SPSS steps and with time became long-term colleagues. I’d also like to express my gratitude to those FG participants and individual interviewees, who I shall not name, but who worked with me together on my research and dedicated parts of their time to answer my questions and allowed me to proceed with my research. A special thank you to André, who took part of this research, and with whom unfortunately I will not be able to share this work. Last, but not least, I would like to thank Dr Christian Atkins, Dr Nii Amoo and Dr Kieran Mervyn who have worked as external reviewers and proof readers. Finally I would like to thank my supervisors, Dr Christine Thomas, Dr Emma Dewberry and initially also Professor Marylyn Carrigan who supported me in the initial phase, as well as the wider MCT team for the support and guidance provided to me.
  • 5. IV Table of contents ABSTRACT .................................................................................................................................................. I DECLARATION ........................................................................................................................................... II ACKNOWLEDGMENTS .............................................................................................................................. III TABLE OF CONTENTS ................................................................................................................................ IV LIST OF FIGURES ........................................................................................................................................ X LIST OF TABLES ........................................................................................................................................ XII LIST OF TERMINOLOGY AND ABBREVIATIONS ......................................................................................... XIII 1 INTRODUCTION .................................................................................................................................. 1 1.1 ENERGY USE AND SUSTAINABILITY ................................................................................................................. 1 1.2 MOTIVATIONS AND BARRIERS TO ENERGY USE ................................................................................................. 3 1.3 ENERGY USE AND BEHAVIOUR CHANGE .......................................................................................................... 5 1.4 AIM OF THE RESEARCH ............................................................................................................................... 6 1.5 RESEARCH QUESTIONS ............................................................................................................................... 7 1.6 RESEARCH PROCESS AND INFORMATION FLOW ................................................................................................ 8 1.6.1 Research process ........................................................................................................................... 8 1.6.2 Information flow ............................................................................................................................ 9 1.7 THE RESEARCH WITHIN THE PORTUGUESE CONTEXT ........................................................................................ 11 2 ENERGY USE AND SUSTAINABILITY ................................................................................................... 15 2.1 DOMESTIC ENERGY USE ............................................................................................................................ 15 2.1.1 Invisibility of energy use .............................................................................................................. 18 2.1.2 Energy use and energy saving at home ....................................................................................... 19 2.2 DETERMINANTS OF ENERGY USE AT HOME .................................................................................................... 20 2.2.1 Social and cultural influences ...................................................................................................... 21 2.2.2 Comfort, convenience and needs ................................................................................................. 23 2.2.3 Norms and energy efficiency ....................................................................................................... 23 2.2.4 Economic influences .................................................................................................................... 25
  • 6. V 2.2.5 Income levels and energy poverty ............................................................................................... 26 2.2.6 Demographic trends .................................................................................................................... 27 2.2.7 The role of infrastructure and technological factors in influencing energy use at home ............ 28 2.2.8 The rebound effect and its influence on determining energy use at home ................................. 29 2.3 CONCLUDING REMARKS ............................................................................................................................ 31 3 ENERGY USE BEHAVIOURS: MOTIVATIONS AND BARRIERS ............................................................... 33 3.1 MOTIVATIONS FOR SAVING ENERGY AT HOME ............................................................................................... 33 3.2 PRO-ENVIRONMENTAL CONCERN: A MOTIVATIONAL VARIABLE OR BARRIER TO BEHAVIOUR? ................................... 33 3.3 BARRIERS TO ADOPTING MORE ENERGY EFFICIENT BEHAVIOURS ........................................................................ 37 3.3.1 Monetary focus as a barrier ........................................................................................................ 37 3.3.2 External/macro barriers: policy based, structural and economic barriers ................................... 37 3.3.3 Knowledge based barriers ........................................................................................................... 39 3.3.4 Cultural – normative and social barriers ..................................................................................... 40 3.4 INDIVIDUAL PSYCHOLOGICAL BARRIERS ........................................................................................................ 40 3.4.1 Habits as a barrier ....................................................................................................................... 41 3.4.2 Comfort as a psychological barrier .............................................................................................. 41 3.4.3 Individual beliefs and self-efficacy as a barrier ............................................................................ 42 3.4.4 Resistance and unwillingness to change as a barrier .................................................................. 44 3.5 CONCLUDING REMARKS ............................................................................................................................ 45 4 ENERGY USE AND INTERVENTION STRATEGIES ................................................................................. 48 4.1 ENERGY USE, INTERVENTIONS AND SUPPORTIVE FRAMEWORKS ......................................................................... 49 4.1.1 Potential intervention layers ....................................................................................................... 53 4.2 BEHAVIOURAL CHANGE, COMMUNICATION AND PERSUASION ........................................................................... 54 4.2.1 Persuasion and communication .................................................................................................. 57 4.2.2 Mental models and communication ............................................................................................ 58 4.2.3 Behavioural change, and relevant and supportive communication ............................................ 59 4.3 STRUCTURAL INTERVENTIONS .................................................................................................................... 59 4.3.1 Financial-economic interventions ................................................................................................ 60 4.3.2 Physical/technical interventions .................................................................................................. 60
  • 7. VI 4.3.3 Legal regulation ........................................................................................................................... 60 4.4 PSYCHOLOGICAL INTERVENTIONS ................................................................................................................ 61 4.4.1 Information provision .................................................................................................................. 62 4.4.2 Commitment and goal setting ..................................................................................................... 65 4.4.3 Behavioural intervention through design .................................................................................... 66 4.4.4 Rewards and punishments .......................................................................................................... 67 4.4.5 Learning theories and modelling ................................................................................................. 69 4.4.6 Social learning community based approaches ............................................................................ 70 4.5 COMBINED STRUCTURAL/PSYCHOLOGICAL INTERVENTIONS ............................................................................. 71 4.5.1 Prompting strategies ................................................................................................................... 71 4.5.2 Feedback provision ...................................................................................................................... 72 4.5.3 Monitoring systems and metering ............................................................................................... 73 4.5.4 Social marketing .......................................................................................................................... 74 4.6 CONCLUDING REMARKS ............................................................................................................................ 77 5 RESEARCH METHODOLOGY AND DESIGN .......................................................................................... 79 5.1 LITERATURE REVIEW ON AVAILABLE METHODS ............................................................................................... 80 5.1.1 Inductive or deductive ................................................................................................................. 80 5.1.2 Subjective or objective ................................................................................................................. 81 5.1.3 Positivism or constructivism ........................................................................................................ 81 5.1.4 Qualitative or quantitative .......................................................................................................... 82 5.1.5 Available research instruments ................................................................................................... 84 5.1.5.1 Surveys and survey questionnaires ...................................................................................................... 85 5.1.5.2 Thematic analysis .................................................................................................................................. 85 5.1.5.3 Content analysis ................................................................................................................................... 86 5.1.5.4 Comparative analysis ............................................................................................................................ 86 5.1.5.5 In-depth individual interviews .............................................................................................................. 86 5.1.5.6 Telephone interviews ........................................................................................................................... 86 5.1.5.7 Grounded theory .................................................................................................................................. 87 5.1.5.8 Action research ..................................................................................................................................... 88 5.1.5.9 Focus groups ......................................................................................................................................... 88
  • 8. VII 5.1.5.10 Direct participant observation ............................................................................................................ 89 5.2 METHODS USED ...................................................................................................................................... 90 5.3 SURVEY QUESTIONNAIRE ........................................................................................................................... 93 5.3.1 Survey questionnaire and data analysis methodology ................................................................ 94 5.3.2 Question added for the specific purpose of this research work ................................................... 96 5.4 FOCUS GROUPS ....................................................................................................................................... 98 5.4.1 Focus group objectives ................................................................................................................ 99 5.4.2 Focus group composition ........................................................................................................... 101 5.5 IN-DEPTH INDIVIDUAL INTERVIEWS ............................................................................................................ 104 5.5.1 Interview objectives ................................................................................................................... 104 5.5.2 Sampling of interviewees ........................................................................................................... 105 5.6 SUMMARY OF EMPIRICAL STUDY METHODS ................................................................................................. 106 5.7 QUALITATIVE DATA ANALYSIS: FOCUS GROUP AND IN-DEPTH INDIVIDUAL INTERVIEWS ......................................... 107 5.8 RESEARCH ETHICS .................................................................................................................................. 108 5.9 SUMMARY ........................................................................................................................................... 109 6 EXPLORING DOMESTIC ENERGY USE ............................................................................................... 111 6.1 CHARACTERISTICS OF DOMESTIC ENERGY USE .............................................................................................. 111 6.1.1 Invisibility as a distinctive characteristic of energy use ............................................................. 111 6.1.2 The fundamental role of domestic energy use .......................................................................... 116 6.2 DETERMINANTS OF DOMESTIC ENERGY USE ................................................................................................ 116 6.2.1 Relation of behaviour and energy use ....................................................................................... 117 6.2.2 Building characteristics .............................................................................................................. 121 6.2.3 Growing number of home appliances ........................................................................................ 121 6.2.4 Energy efficient home appliances and overall energy prices ..................................................... 122 6.2.5 The evolution of cultural and social norms ................................................................................ 125 6.3 CONCLUDING REMARKS .......................................................................................................................... 127 7 FACTORS INFLUENCING ENERGY USE AT HOME .............................................................................. 135 7.1 MOTIVATIONAL VARIABLES AND ENERGY EFFICIENT BEHAVIOURS .................................................................... 135 7.1.1 The motivation for saving money .............................................................................................. 135
  • 9. VIII 7.1.2 Pro-environmental behaviour and pro-social motivations ........................................................ 137 7.1.3 Needs and expectations and its relation to motivation for saving energy ................................ 144 7.2 BARRIERS FOR ADOPTING MORE ENERGY EFFICIENT BEHAVIOURS ..................................................................... 144 7.2.1 External/macro barriers: policy based, structural and economic barriers ................................. 145 7.2.2 Knowledge based barriers ......................................................................................................... 147 7.2.3 Cultural-normative-social barriers ............................................................................................. 152 7.3 INDIVIDUAL PSYCHOLOGICAL FACTORS AS A BARRIER ..................................................................................... 154 7.3.1 Habits as an obstacle to the adoption of more energy efficient behaviours ............................. 154 7.3.2 Comfort and convenience .......................................................................................................... 157 7.3.3 Efficacy and outcome expectations ........................................................................................... 158 7.3.4 Resistance to and unwillingness to change ............................................................................... 161 7.4 CONCLUDING REMARKS .......................................................................................................................... 163 8 INTERVENTION STRATEGIES AND PERCEIVED EFFECTIVENESS ......................................................... 170 8.1 COMMUNICATION DESIGN AND PERSUASION .............................................................................................. 171 8.2 STRUCTURAL INTERVENTIONS .................................................................................................................. 173 8.2.1 Rewards and punishments ........................................................................................................ 173 8.2.2 Incentives and samples .............................................................................................................. 174 8.2.3 Labelling .................................................................................................................................... 175 8.2.4 Demonstrating and facilitating ................................................................................................. 177 8.2.5 Intervention through design ...................................................................................................... 178 8.3 PSYCHOLOGICAL INTERVENTIONS .............................................................................................................. 179 8.3.1 Targeted face-to-face information ............................................................................................ 179 8.3.2 Information and communication campaigns ............................................................................ 180 8.3.3 Education interventions ............................................................................................................. 183 8.3.4 Community based interventions ................................................................................................ 184 8.4 COMBINED STRUCTURAL/PSYCHOLOGICAL INTERVENTIONS ............................................................................ 185 8.4.1 Information, feedback and monitoring equipment ................................................................... 185 8.4.2 Smart metering and prompting strategies ................................................................................ 187 8.4.3 Information, feedback and energy bills ..................................................................................... 188
  • 10. IX 8.5 CONCLUDING REMARKS .......................................................................................................................... 188 9 CONCLUSION .................................................................................................................................. 196 9.1 SPECIFIC ANSWERS TO THE RESEARCH QUESTIONS ........................................................................................ 196 9.1.1 RQ1: What explains energy use at home? ................................................................................. 196 9.1.2 RQ2: What influences energy use at home? .............................................................................. 197 9.1.3 RQ3: What is the potential role of intervention strategies on energy use at home? ................ 199 9.2 KEY FINDINGS ....................................................................................................................................... 200 9.2.1 Importance to challenge the understanding of normal ............................................................. 201 9.2.2 Invisibility of energy and its implications ................................................................................... 202 9.2.3 Financial motivations to save energy ........................................................................................ 202 9.2.4 Knowledge, competence and self-efficacy ................................................................................. 203 9.2.5 Energy efficient behaviour and outcome efficacy ...................................................................... 203 9.3 LIMITATIONS OF THE RESEARCH ................................................................................................................ 204 9.4 SUGGESTED FUTURE RESEARCH ................................................................................................................ 204 REFERENCES .......................................................................................................................................... 206 APPENDICES .......................................................................................................................................... 226 APPENDIX I: ENERGYPROFILER SURVEY QUESTIONNAIRE .......................................................................................... 226 APPENDIX II: REDUCED VERSION - FG QUESTIONNAIRE BEFORE DISCUSSION ................................................................ 234 APPENDIX III: CONSUMER INTERVIEW ROADMAP ................................................................................................... 235 APPENDIX IV: PRACTITIONER INTERVIEW ROADMAP ............................................................................................... 238 APPENDIX V: LIST OF ANSWERS FOR QUESTION 6 OF EP SURVEY QUESTIONNAIRE REGARDING ENERGY SAVING REPORTED BEHAVIOURS .................................................................................................................................................. 240 APPENDIX VI: – LIST OF ANSWERS FOR QUESTION 15 OF EP SURVEY QUESTIONNAIRE REGARDING ENERGY SAVING REPORTED BEHAVIOURS .................................................................................................................................................. 241 APPENDIX VII: VARIABLES DEFINED DURING ENERGYPROFILER STUDY ......................................................................... 242 APPENDIX VIII: – LIST OF ANSWERS FOR QUESTION Q16 OF EP SURVEY QUESTIONNAIRE (REPORTED BARRIERS AND CONSTRAINTS) ................................................................................................................................................ 243 APPENDIX IX: – LIST OF IDENTIFIED BARRIERS DURING THE FG ................................................................................. 244 APPENDIX X: – SAMPLE DISTRIBUTION WITH REGARD TO REGION, GENDER, AGE GROUPS AND RURAL/URBAN AREA ............ 245
  • 11. X List of Figures FIGURE 1-1: THE THREE MAIN PILLARS OF SUSTAINABLE DEVELOPMENT: ECONOMIC GROWTH, ENVIRONMENTAL PROTECTION AND SOCIAL EQUALITY, (KENNEDY, 2011). ................................................................................................................. 2 FIGURE 1-2: THE RELATION BETWEEN INDIVIDUAL ENERGY RELATED BEHAVIOUR AND BARRIERS TO CHANGE, (BARENERGY, 2011). ................................................................................................................................................................... 4 FIGURE 1-3: SCHEMATIC REPRESENTATION OF RESEARCH DESIGN. .................................................................................... 8 FIGURE 1-4: SCHEMATIC REPRESENTATION OF INFORMATION FLOW. ............................................................................... 10 FIGURE 2-1: DISTRIBUTION OF ENERGY CONSUMPTION IN HOUSEHOLDS BY SOURCE TYPE IN 2010, (INE, 2011; INE I.P./DGEG, 2011). ....................................................................................................................................................... 17 FIGURE 2-2: DISTRIBUTION OF ENERGY CONSUMPTION IN HOUSEHOLDS BY USE TYPE IN 2010, (INE I.P./DGEG, 2011). ........ 18 FIGURE 2-3: MAIN FACTORS INFLUENCING CONSUMER BEHAVIOUR AND EMERGENCE OF CONSUMPTION PRACTICES, (EEA, 2013). ................................................................................................................................................................. 20 FIGURE 2-4: AN ACTOR-STRUCTURE MODEL OF CONSUMPTION, (ADAPTED FROM SPAARGAREN AND VAN VLIET (2000)). ....... 22 FIGURE 3-1: DIAGRAMMATIC REPRESENTATION OF THE CONDITIONAL RELATIONS BETWEEN EFFICACY BELIEFS AND OUTCOME EXPECTANCIES (ADAPTED FROM BANDURA (1977B), P. 350). ............................................................................... 43 FIGURE 4-1: REDUCING CAR USE: FACTORS AFFECTING BEHAVIOURAL CHANGE, (PRENDERGRAST ET AL. 2008, P. 104). ........... 50 FIGURE 4-2: DIAGRAMMATIC REPRESENTATION OF THE 4E’S MODEL, (DEFRA, 2008, P. 53). ............................................ 52 FIGURE 4-3: MINDSPACE’S INFLUENCES ON BEHAVIOUR, (DOLAN, 2010). ...................................................................... 52 FIGURE 4-4: THE RELATION BETWEEN MATERIAL, SOCIAL AND INDIVIDUAL CONTEXTS, ADAPTED FROM SOUTHERTON ET AL. (2011). ...................................................................................................................................................... 53 FIGURE 4-5: THE RELATION BETWEEN ENERGY USE DETERMINANTS, MOTIVATIONS, BARRIERS TO CHANGE AND TYPES OF INTERVENTION, ADAPTED FROM, (BARENERGY, 2011). ........................................................................................ 54 FIGURE 5-1: RESEARCH DESIGN FROM INITIAL FRAMING TO IMPLEMENTATION. ................................................................. 79 FIGURE 7-1: AVERAGE VALUES FOR RISK PERCEPTION OF CLIMATE CHANGE AND ATTITUDE, KNOWLEDGE AND ENVIRONMENTAL BEHAVIOUR [N=1.014, F (2.89 , 2914.70) = 434.73, P = .000, Η 2 =.57], (ENERGYPROFILER, 2011). .................... 139 FIGURE 7-2: VALUES FOR ATTITUDE, KNOWLEDGE AND RESPONSIBILITY TOWARDS ENERGY USE [N=1.014; F (2.89 , 2914.70) = 434.73, P = .000, Η 2 =.57], (ENERGYPROFILER, 2011). ................................................................................... 140 FIGURE 7-3: REPORTED PRO-ENVIRONMENTAL BEHAVIOURS [N=1.014], (ENERGYPROFILER, 2011). ................................. 141 FIGURE 7-4: REASONS FOR NOT SAVING ENERGY AT HOME – RESPONSES FROM FGS ........................................................ 145 FIGURE 7-5: FREQUENCY OF CATEGORY GROUPS OF BARRIERS DURING FGS. ................................................................... 145
  • 13. XII List of Tables TABLE 5-1 – FOCUS GROUP ROADMAP AND TECHNIQUES USED. ................................................................................... 100 TABLE 5-2 – SUMMARY OF RESEARCH ACTIVITIES. ..................................................................................................... 106 TABLE 5-3 – CONTENT ANALYSIS. ........................................................................................................................... 108 TABLE 6-1 – RELATION IN BETWEEN CHAPTER AND RESEARCH QUESTIONS. ..................................................................... 111 TABLE 6 -2 – REPORTED ENERGY EFFICIENT BEHAVIOURS [N=1.014], (ENERGYPROFILER, 2011). ...................................... 119 TABLE 6-3 – SUMMARY OF FINDINGS RELATING TO RQ1 ............................................................................................ 128 TABLE 7-1 – COMPOSITE SCALES [N=1.014, F (2.89 , 2914.70) = 434.73, P = .000, Η2 =.57], (ENERGYPROFILER, 2011).. ....................................................................................................................................................................... 138 TABLE 7-2 – SUMMARY OF FINDINGS RELATING TO RQ2. ........................................................................................... 164 TABLE 8-1 – SUMMARY OF FINDINGS RELATING TO RQ3 ............................................................................................ 193
  • 14. XIII List of Terminology and Abbreviations Attitudes: “relatively enduring predisposition to respond favourably or unfavourably” towards something, (Simons, 1976, p. 80) influencing consumption patterns, recommendation to others, beliefs and intentions”, (Schiffman & Kanuk, 1999, pp. 199-200) Attitude-Behaviour Gap: positive attitudes do not necessarily lead to behaviour, (Kollmuss & Agyeman, 2002), a phenomenon also known within pro-environmental behaviours, since general positive pro- environmental attitudes do not seem to be particular important predictors of environmentally significant behaviour, (Bamberg, 2003; Poortinga, Steg, & Vlek, 2004; Schultz, Oskamp, & Mainieri, 1995; Thøgersen, 2004). Behaviour: the result of multiple conscious and unconscious processes as well as internal (psychological variables such as norms, beliefs or values) and external variables (e.g. social, economic physical), drivers and constraints, personal capabilities, or habits and routines, (Jackson, 2005; Nye, Whitmarsh, & Foxon, 2010; Stern, 2000). Behavioural change intervention: Generic and specific interventions to support a change in behaviour at the individual and population level. In the environmental context it can be understood as a change in the patterns of consumption of resources, (Committee on Climate Change [CCC], 2012). Behaviour-Based Programs: Energy efficiency programs that utilize an understanding of how individuals interact with energy in order to decrease energy demand, (American Council for an Energy-Efficient Economy [ACEEE], n.d.). Beliefs: psychological state in which an individual holds a proposition or premise to be true, (Schwitzgebel, 2010), which in terms of behaviour could be the “salient information, relevant to the behaviour”, (Ajzen, 1991, p. 189). Biocapacity: the area of land and productive oceans actually available to produce renewable resources and absorb CO2 emissions, (World Wide Fund for Nature [WWF], 2012). Biocapacity quantifies nature’s capacity to produce renewable resources, provide land for built-up areas and provide waste absorption services such as carbon uptake. Biocapacity acts as an ecological benchmark against which the Ecological Footprint can be
  • 15. XIV compared. Both the Ecological Footprint and biocapacity are expressed in a common unit called a global hectare, where 1 gha represents a biologically productive hectare with world average productivity. CID: For the purpose of this research CID stands for ‘Consumer Interview’ meaning the 3 interviews that were performed to consumers selected from the focus group that had been performed as part of the empirical study. Collective efficacy: “sense of collective efficacy” does exist where individuals can solve their problems and improve their lives through concerted effort, (Bandura, 1986, p. 449). Comprehensive Home Energy Audits: An assessment of a home’s energy use that includes a visual inspection, diagnostic testing, analysis, and a list of proposed improvements, ending with guidance to complete the work, or actual completion of the work, (ACEEE, n.d.). Concept, conception or construct: abstract object, or a mental representation, e.g. wellbeing, depression, poverty, achievement, family. They are not only the building blocks of theory, but they also form the link between theory and empirical research, (Bergman, 2010). Consumerism: emphasis on or preoccupation with the acquisition of consumer goods, (Oxford University Press, 2013). Consumption: the “human transformation of materials and energy”, (Royal Society of London & U.S. National Academy of Sciences, 1997, p. 684), requiring the “selection, use, disposal, and recycling of goods and services”, (Campbell, 1995, p. 102). Curtailment behaviours: behaviours that must be performed frequently, involving repetitive efforts to reduce energy, and involve more operational day to day habits and routines, such as lowering the thermostat, turning lights and appliances off, (Abrahamse, Steg, Vlek, & Rothengatter, 2005; Gardner & Stern, 2002). Demand-Side Management: The planning, implementation, and monitoring of utility activities designed to encourage consumers to modify patterns of electricity usage, including the timing and level of electricity demand, (U.S. Energy Information Agency [EIA], 2013).
  • 16. XV Descriptive norm: what most people do; the perception individuals hold about what is normal in a given situation, (Cialdini, Kallgren, & Reno, 1991; Cialdini, Reno, & Kallgren, 1990). Dwelling: a self-contained unit of accommodation, (Department for Communities and Local Government [DCLG], 2012). Ecological Footprint: tracks humanity’s demands on the biosphere by comparing humanity’s consumption against the Earth’s regenerative capacity, or biocapacity, by calculating the area required to produce the resources people consume, the area occupied by infrastructure, and the area of forest required for sequestering CO2 not absorbed by the ocean, (Galli et al., 2007; Kitzes et al., 2009; Wackernagel et al., 2002). Efficacy expectations: “the conviction that one can successfully execute the behaviour required to produce outcomes”, (Bandura, 1977a, p. 193). Efficiency behaviours: infrequent type of behaviours, like for example one-off actions, which often entail an investment, such as loft or cavity wall insulation, or buying an energy efficient air conditioner. Commonly also referred to as ‘efficiency behaviours’ or ‘investment behaviours’, (Abrahamse et al., 2005; Gardner & Stern, 2002; Kempton, Boster, & Hartley, 1995). Energy Audit: assessment of a home's energy use. These include a number of different types of surveys, including (in increasing order of cost and complexity): online audits, in-home home energy surveys, diagnostic home energy surveys, and comprehensive home energy audits, (ACEEE, n.d.). Energy Conservation: reduction in the amount of energy consumed in a process or system, or by an organization or society, through economy, elimination of waste, and rational use, (BusinessDictionary, n.d.). Saving energy by doing with less or doing without (e.g., setting thermostats lower in winter and higher in summer; turning off lights; taking shorter showers; turning off air conditioners; etc.), (ACEEE, n.d.). Energy efficiency: ratio of ‘useful’ outputs to energy inputs for a system. The system in question may be an individual energy conversion device (e.g. a boiler), a building, an industrial process, a firm, a sector or an entire economy, (Sorrell, 2007). Percentage of total energy input to a machine or equipment that is consumed in useful work and not wasted as useless heat, (BusinessDictionary, n.d.).
  • 17. XVI Energy efficiency gap: difference between the ‘actual energy efficiency’ and the ‘potential efficiency’, meaning part of the efficiency gain due to technological developments is being ‘taken back’, (Feenstra, Backhaus, & Heiskanen, 2009). Energy Efficiency Measure: particular good or practice that provides an energy efficiency benefit. Upgraded insulation, energy efficient appliances, and adjusting a boiler’s limit control are examples of measures, (ACEEE, n.d.). Energy Efficiency Potential: amount of energy savings possible, (ACEEE, n.d.). Energy Management System: computerized system for fully automatic control of HVAC, lighting, refrigeration, and other commercial building subsystems in order to accurately manage and monitor indoor temperature, comfort, and environmental quality. An EMS often saves energy and money by operating systems only when needed and by allowing time-of-day scheduling and peak load shedding control, (ACEEE, n.d.). Energy services: these are the services that people gain from using energy and include warm rooms, hot water, a well-lit home and refrigerated food, (Environmental Change Institute [ECI], 2005) Energy Performance Certificate (EPC): The certificate provides a rating for residential and commercial buildings, showing their energy efficiency based on the performance of the building itself and its services (such as heating and lighting). EPCs are required whenever a building is built, sold or rented out, (CCC, 2012). Environmentally Significant Behaviour (ESB): a behaviour that does not “threaten human health, welfare, or other things people value”, (Stern, 1997, p. 15) and that is characterized by its “positive impact on the availability of materials or energy from the environment and/or by the extent to which the behaviours positively alter the structure and dynamics of ecosystems or the biosphere”, (Stern, 2000, p. 408). EP: For the purpose of this research EP stands for ‘energyprofiler study’ as had been conducted within the empirical work. FG: For the purpose of this research FG stands for ‘Focus Group’ as they had been conducted within the empirical work.
  • 18. XVII Habits: Even though this work is aware of the different understanding from the fields of psychology and sociology of the habits construct, it is not within the scope of this research to advocate for one or the other understanding. As a result of this, habits, routines and practices might be used interchangeably meaning individuals running on autopilot, (Grist, 2010). Household: one person or a group of people who have the accommodation as their only or main residence and either share at least one meal a day, or share the living room, (DCLG, 2012). Information-Behaviour Gap: disconnection between knowledge hold and behaviour outcome, (Jackson, 2005; Schultz, 2002; Southerton, McMeekin, & Evans, 2011; Stern, 1999). Injunctive social norm: what ought to be done; explicitly reflect the moral rules and guidelines of the social group, (Cialdini et al., 1990, 1991). Lifestyles: the way people live their life, fulfil their needs and aspirations, through the mediation of goods that are closely linked to material and resource flows, (Backhaus, Breukers, Mont, Paukovic, & Mourik, 2012). Moral norms: an altruistic behaviour results once a moral norm is activated. This activation occurs once an individual becomes aware that his or her behaviour has possible negative consequences for others and is willing to take personal responsibility for the others’ well-being, (Schwartz, 1970, 1977). Norms: “rules and standards that are understood by members of a group and that guide and/or constrain social behaviour without the force of laws”, (Cialdini & Trost, 1998, p. 152). Outcome expectancy: “a person’s estimate that a given behaviour will lead to certain outcomes”, (Bandura, 1977a, p. 193). Perceived Behavioural Control: individual’s belief about the easiness or difficulty of performing a given behaviour, (Ajzen & Madden, 1986). Personal Carbon Alliances: With PCAs, each adult has an equal carbon allocation to cover purchases of gas, electricity, petrol and aviation. The PCA brings home to the individual, in a forceful way, the amount of carbon being released through daily activities, (ECI, 2005).
  • 19. XVIII Personal norms: feelings of strong moral obligation that people experienced to engage in pro-social behaviour, (Schwartz, 1970, 1977). PID: For the purpose of this research PID stands for ‘Provider Interview’, meaning the 3 interviews that were performed to people working for intervention providers within the energy area. Price elasticity: the percentage change in one variable following a percentage change in another, holding other variables constant, (Sorrell, 2007). Rebound effect: also known as ‘take-back effect’, is measured by the difference between the projected and actual savings due to increased efficiency and is normally expressed as a percentage of the expected energy savings from an energy efficiency improvement, (Sorrell, 2007). Self-efficacy: “people’s judgments of their capabilities to organise and execute courses of action required to attain designated types of performances”, (Bandura, 1986, p. 395). Single-Action Bias: tendency people have to engage into single corrective actions and therefore ‘doing their bit’ thus increasing the resistance and decreasing the need of taking additional actions, (Weber, 1997). Smart Meters: An advanced electricity meter that uses real time sensors to provide information on power consumption and price, (ACEEE, n.d.). Social Marketing: the application of marketing principles and tools to achieve socially desirable goals, (Andreasen, 1995; Kotler & Zaltman, 1971). Social Norms: unwritten rules and expectations that frame appropriate and inappropriate expectations and behaviours within a group of individuals, (Lewis, 1969). Spillover effect: term used to describe the transferability across behaviours and contexts between one kind of environmental behaviour and another, (Thøgersen & Ølander, 2002). Subjective norm: individual perception about what other people who are important to him/her think of the specific behaviour, rather than the individual personal belief about the morality of the given behaviour, (Ajzen & Fishbein, 1980).
  • 20. XIX Sustainable development: “the kind of development that meets the needs of the present without compromising the ability of future generations to meet their own needs”, (United Nations [UN], 1987). Sustainable consumption: “the use of goods and services that respond to basic needs and bring a better quality of life, while minimising the use of natural resources, toxic materials and emissions of waste and pollutants over the life cycle, so as not to jeopardise the needs of future generations”, (Norwegian Ministry of the Environment, 1994). Values: Considered by some, as the hardest thing to change, (Andreasen, 1995; Kotler, Roberto, & Roberto, 1989), values might be overall defined as “a desirable trans-situational goal varying in importance, which serves as a guiding principle in the life of a person or other social entity”, (Schwartz, 1992, p. 21).
  • 21. 1. Introduction 1 1 Introduction Current energy use in the developed world is considered to be unsustainable with energy consumption and production patterns undermining sustainable development and the equitable distribution of resources worldwide, (Intergovernmental Panel on Climate Change, [IPCC], 2007; Stern, 2007). To achieve more sustainable energy use levels requires a combination of cultural and technological advances and innovation in the design of social and institutional systems and systems of production and consumption, (Cole, 2011). However, although such changes at societal level are likely to lead to some reductions in energy use at the household level, it is recognised that significant change in household energy consumption is unlikely to occur without changes in individuals’ energy usage behaviours. To achieve the goal of sustainable levels of household energy use requires a clear understanding of energy use at home and what influences current energy use behaviours so to adopt more energy efficient behaviours, (Darby, 2006; Janda, 2011). This research aims to explore how the adoption of more energy efficient behaviours at home could be encouraged. With this the research has the objective to better understand the different determinants of energy use at home, the role of motivations and barriers that drive energy use at home, and the potential role of interventions to promote behavioural change. This chapter firstly sets the context for the research by describing the need for working towards a more sustainable society and the important role that energy use plays in this. It then considers the role of individuals’ energy use behaviours; what motivates them and what barriers they face and how they might be influenced to reduce domestic energy use. The chapter concludes with the research aims, the research questions and the structure of the thesis. 1.1 Energy use and sustainability Energy use underpins most aspects of modern life. It is important in the production of goods, most services and the way we live. However, many forms of energy, in particular fossil fuels, contribute to environmental problems, such as climate change and local air pollution, (Organization for Economic Co-operation and Development, (OECD], 2012). What we desire in a modern lifestyle therefore seems to come at the cost of undesired environmental problems and this is particularly prevalent for developed countries, (UN, 1987;
  • 22. 1. Introduction 2 IPCC, 2007; Stern, 2007). Recent trends regarding increasing global population, (U.S. Census Bureau, 2011; UN, 2011) and increasing material consumption, as a consequence of the growing level of perceived needs, have exacerbated this problem, (The Royal Society, 2012). It has therefore been argued that changes in current lifestyles will be required to achieve a sustainable level at which the needs of the present are met without compromising the environment for future generations so as to allow for the long-term use of natural resources for current as well as future generations, (Backhaus et al., 2012; IUCN, UNEP, & WWF, 1991; UN, 1987). Development should thus be socially and morally just, ethically acceptable and economically sound, with environmental indicators as important as economic indicators, (Leal Filho, 2011; UN, 1987). As such, sustainable development implies a balanced intersection of economic, environmental and social factors, (Elkington, 1997), (Figure 1-1). Figure 1-1: The three main pillars of sustainable development: economic growth, environmental protection and social equality, (Kennedy, 2011). However, evidence suggests that it will become increasingly difficult to meet such expectations and commitments, (WWF, 2012), within a fast growing human population that has increased from 1.6 billion in 1900 to 7 billion in 2011, (U.S. Census Bureau, 2011) and is forecast to reach just over 9.3 billion by 2050, (UN, 2007). This rapid and widespread change in the global human population, coupled with unprecedented levels of consumption, has implications for finite planetary resources and presents a challenge not only to the environment, but also to human health and wellbeing, (The Royal Society, 2012). What citizens from developed countries perceive as being a, ‘normal lifestyle’, might not be sustainable in a global context of population growth and depleting natural resources. This becomes, in particular, apparent when considering the ecological footprint that measures the demands of humanity on the biosphere by comparing
  • 23. 1. Introduction 3 consumption against the Earth’s regenerative capacity, or biocapacity, (WWF, 2012). The ecological footprint shows a consistent trend of overconsumption for the few last decades, with a growing biocapacity deficit. Humanity’s annual demand on the natural world has exceeded what the Earth can annually renew since the 1970s. In 2008 it exceeded the Earth’s biocapacity by more than 50 per cent, which means it would take 1.5 years for the Earth to fully regenerate the renewable resources consumed in one year, (Galli et al., 2007; Kitzes et al., 2009; Poumanyvong & Kaneko, 2010; Wackernagel et al., 2002; OnePlanetLiving, n.d., WWF, 2012). At the individual human level the ecological footprint is influenced by the choices individuals make on what they eat, what products they purchase, how they heat/cool their homes and how they travel, (WWF, 2012). A challenge of our age could thus be seen in decoupling human progress from resource use and environmental decline, (KPMG, 2012). This is to say decoupling unsustainable human needs, wants and expectations and rebuilding these in a more sustainable way. As long as this is not achieved however, there will be a conflict between limitless needs vs. limited resources and the need to define the boundaries of what is understood as ‘sustainable’, ‘normal’ or ‘socially acceptable’ consumption, (Norwegian Ministry of the Environment, 1994; UN, 1987, 1992). Sustainability in relation to energy use can also, “be understood as a continuous learning process that occurs when a given society acquires the necessary knowledge to reduce its energy consumption without diminishing its quality of life or creating new social inequalities”, (Tabara et al., 1999, p. 1). Therefore the focus of fulfilling individual needs in a more sustainable way is a core concept of this thesis; reinforcing that sustainability in energy terms should not mean losing wellbeing, but rather doing things in a different way. Part of that different way requires individual behavioural change and an understanding of the motivations and barriers for change. 1.2 Motivations and barriers to energy use Motivations are factors encouraging, or influencing, a change in behaviour, or maintaining a current behaviour and barriers those that obstruct or limit change. Saving money and protecting the environment are the first and second most frequently reported motivations for saving energy at home, (Eurobarometer, 2011a). However, they are not often fully realized as reduced energy use might be perceived as negatively impacting comfort or wellbeing. In such an equation the gain and motivation of maintaining old habits can
  • 24. 1. Introduction 4 have a higher priority than that of saving money and protecting the environment. In this situation the gain and motivation of maintaining old habits constitute a barrier to the adoption of more energy efficient lifestyles, (Jackson, 2005; Prendergrast, Foley, Menne, & Isaac, 2008). Individuals’ own habits, or their compliance to existing and commonly accepted standards and social norms, can work as motivations to maintaining existing behaviours, (EEA, 2013; Shove, 2003). To achieve a change towards energy efficient behaviour would thus require understanding the respective barriers, (Homans, 1958), as well as the underlying attitudes and values, (Andreasen, 1995; Homans, 1958; Kotler et al., 1989). This interplay between barriers and behaviours is depicted in Figure 1-2 and Throne-Holst, Strandbakken, and Stø (2008) suggest that it consists of six barrier groups. Figure 1-2 highlights the interplay in terms of macro and micro factors between the individual, surrounding setting and infrastructure that could motivate, enable and reinforce individual behavioural change as well as illustrate the complexity of such relations. Figure 1-2: The relation between individual energy related behaviour and barriers to change, (Barenergy, 2011). In accordance with Throne-Holst et al. (2008), barriers toward the adoption of more energy efficient behaviours could be grouped as: (1) Information/knowledge barriers, where people are lacking relevant information regarding energy efficiency measures that they could adopt. (2) Physical and structural barriers, where the existing physical structure of dwellings and of society can be a disincentive and tend to lock people into less sustainable behaviours.
  • 25. 1. Introduction 5 (3) Political barriers, such as laws and regulations that frame and determine the ability to change individual behaviours. (4) Cultural-normative barriers, as people do not live in isolation, and social and cultural norms may restrict engagement in more energy efficient behaviours, even if they hold a positive opinion towards them. (5) Economic barriers, since more energy efficient solutions can be expensive, the higher prices may therefore discourage people from becoming more efficient in their energy use. (6) Individual-psychological barriers, as a pre-determinant of the adoption of more energy efficient behaviours. This is the individual willingness to change behaviour that is influenced by individual’s personal habits and comfort zones, including for instance the concept of self-efficacy, (Bandura, 1986), or Perceived Behaviour Control, (Ajzen, 1991). As such, any given motivation might have to face a number of barriers from different barrier groups. To achieve behavioural change towards the adoption of more energy efficient behaviours therefore would not only require understanding all of the respective barriers, but also the underlying attitudes and values, and subsequently means to overcome each of them. 1.3 Energy use and behaviour change Energy saving can be realized through infrastructural development, increasing technological development and deployment, the introduction of more energy efficient materials and appliances and also through the rational and sustainable use of energy at home, based on the adoption of more energy efficient behaviours. For decades, research has mainly focused on the technical component, such as providing more energy efficient home appliances or building materials and only more recently has attention been directed to the non-technical components and to the contribution of how people behave and interact with home appliances and infrastructures, in terms of energy use at home, (EEA, 2013). The reasons for a focus on technology might have been that it was expected to be ‘easier’ to influence efficiency behaviours that are characterized by one-off actions, instead of changing curtailment behaviours, which must be performed frequently, (Abrahamse et al., 2005; Gardner & Stern, 2002). However, focusing on efficiency behaviours usually involves the need for an initial investment, which can itself act as a barrier. But even in the event
  • 26. 1. Introduction 6 that those barriers can be overcome and financial savings generated, the energy saved might subsequently be used for other energy using activity, or to increase the number of home appliances that people have. It can thus lead to what is known as a ‘rebound-effect’ where the energy saving potential is not realized in practice, (Khazzoom, 1980). For these reasons the contribution that curtailment behaviours can play should not be underestimated and interventions that attempt to change behaviours must, ultimately, need to lead to long-term behaviour change to be successful. The literature shows a diversity of existing intervention strategies and types that could support and enable behavioural change and can be grouped into two broader categories: (a), structural and (b), psychological interventions, (Poortinga et al., 2004; Steg, 2003). Structural interventions aim to change the (social) context in which behavioural decisions take place, based on the belief that by altering the conditions on which behaviour is based, the behaviour will then change in accordance. In contrast, psychological interventions aim at changing existing perceptions, knowledge, attitudes, norms and values, (i.e. individual, micro-level variables). The underlying assumption here is that by changing these determinants, behaviour will change accordingly. Structural and psychological interventions have been employed to encourage household energy conservation with varying degrees of success, (Abrahamse et al., 2005; Geller, Harrington, Rosenfeld, Tanishima, & Unander, 2006; Heiskanen, Mourik, Feenstra, & Pariag, 2009; Kurz, 2002; Southerton et al., 2011). A number of studies apparently suggest that success, when it occurs, rarely survives when the change interventions are discontinued, (Abrahamse et al., 2005; Heiskanen et al., 2009; Kurz, 2002; Lutzenhiser, 2002). Despite the growing body of existing research and evidence, there appears however still to be no clear evidence within the literature on the potential long-term effectiveness of change interventions within the field of energy use at home; an area that this work attempts to explore further. 1.4 Aim of the research The overall aim of this research is to explore how the adoption of more energy efficient behaviours at home could be encouraged. Within this, a first objective is to provide an overview of the nature of energy use at home and the factors that influence energy use, (chapter 2). Subsequently the research investigates whether the same set of factors and conditions can be found within the empirical study in Portugal, (chapter 6). Secondly, this research has the objective to advance on the theory of motivating, enabling and
  • 27. 1. Introduction 7 reinforcing factors that could promote the adoption of more energy efficient habitual behaviours and practices at a household level, (chapter 3), as well as for the Portuguese context, (chapter 7). Thirdly, this research has the objective to explore the potential effectiveness of change interventions within the field of energy use at home and the different types of interventions that might be used, (chapter 4) and how those are perceived and evaluated within the examples of practice in Portugal, (chapter 8). The reason for the geographic focus of this research was two-fold. Firstly, the researcher was aware of an apparent scarcity of existing studies that investigated domestic energy use in Portugal and secondly, for pragmatic reasons, as the researcher is based in Portugal and cognisant of the social context of household energy use. The geographical scope has been limited to northern Portugal to explore the topic of research in more depth. 1.5 Research Questions Based upon the review of the literature as well as driven by the thesis aim and objectives, the following research questions, (RQ), have been derived: Research Question 1: What explains energy use at home? a) What are the characteristics of energy use at home? b) What are determinants of energy use at home? c) How do individuals understand their energy use at home? Research Question 2: What influences energy use at home? a) What are motivational variables for adopting more energy efficient behaviours? b) What are the barriers for adopting more energy efficient behaviours? c) How do individual psychological factors influence energy use? Research Question 3: What is the potential role of intervention strategies on energy use at home? a) What are perceived requirements of intervention strategies? b) What are individual perceptions on the effectiveness of intervention strategies?
  • 28. 1. Introduction 8 1.6 Research process and information flow This section provides an overview of the research process and information flow. 1.6.1 Research process To fully explore the research questions, this research uses a mixed methods design, where qualitative and quantitative methods are combined. The use of both qualitative and quantitative methods was seen to be necessary to encompass differing aspects of the research, as explained in Chapter 5. Figure 1-3 is a schematic representation of the research design. Figure 1-3: Schematic representation of research design. As can be seen in Figure 1-3, the research starts with a comprehensive literature review of the theoretical approaches to understanding human behaviour in general and more specifically, those concerned with more energy efficient lifestyles. To better explore the topic, the literature around energy use and sustainability was reviewed to locate discussion and identify the reasons why people are expected to use less energy at home. In addition, the literature within the field of behavioural change, more generally as well as within an energy context, has been reviewed. Chapter 2 explores the use of energy at a household
  • 29. 1. Introduction 9 level and its relation to sustainability. Chapter 3 reviews the literature on understanding human behaviour and in particular, of energy related behaviours at home. This section also looks at motivating factors and barriers related to individual behavioural change within the energy area. Chapter 4 looks at the potential effectiveness of change interventions within the field of energy use at home and the different types of interventions that might be applied. This chapter includes a reflection around theories of persuasion and their role in frameworks for change such as social marketing. Chapter 5 details the research methodologies adopted and the research design for the empirical phase of this research. Chapter 6, 7 and 8 present and discuss the findings from the empirical phase of this research. These include the results from the energyprofiler national survey, exploratory focus groups and in-depth interviews. Finally, chapter 9 presents the research conclusions, drawing on the theoretical and empirical findings and discusses the contribution of this research. 1.6.2 Information flow Figure 1-4 provides a schematic representation of the information and how the respective chapters and sections inform each other. As can be seen, in Figure 1-4 there are three direct information strings that start in chapter 1, (sections 1.1, 1.2, 1.3), which are then followed up in the literature review, (chapters 2, 3, and 4) and subsequently looked at empirically, (chapters 6, 7, and 8).
  • 30. 1. Introduction 10 Figure 1-4: Schematic representation of information flow. Chapter(1(*(Introduction 1.1.#Energy#use#and# sustainability# 1.2.#Motivations#and# barriers#to#energy#use 1.3.#Energy#use#and# behaviour#change Chapters(2,(3(and(4(*(Literature(Background( 2.#Energy#use#and# sustainability 3.#Energy#use#behaviours:# motivations#and#barriers 4.##Energy#use#and# Intervention#strategies Chapters(6,(7(and(8(*(Empirical(Work( 6.#Exploring#domestic# energy#use#in#Portugal 7.#Factors#influencing# energy#use#at#home 8.#Intervention#strategies# and#perceived# effectiveness Chapter(9(*(Conclusion 9.2.1.#RQ1 9.2.2.#RQ2 9.2.3.#RQ3 RQ1:(What(explains(energy(use(at(home? X RQ1a.#What#are#the#characteristics#of#energy# use#at#home? X RQ1b.#What#are#determinants#of#energy#use#at# home? X RQ1c.#How#do#individuals#understand#their# energy#use#at#home? RQ2:(What(influences(energy(use(at(home? X RQ2a.#What#are#motivational#variables#for# adopting#more#energy#efficient#behaviours? X RQ2b.#What#are#the#barriers#for#adopting#more# energy#efficient#behaviours?# X RQ2c.#How#do#individual#psychological#factors# influence#energy#use? X RQ3:(What(is(the(potential(role(of(intervention( strategies(on(energy(use(at(home? X RQ3a.#What#are#perceived#requirements#of# intervention#strategies? X RQ3b.#What#are#individual#perceptions#on#the# effectiveness#of#intervention#strategies? X Thesis(information(flow Relation(between(sections(and(Research(Questions((RQ,(section(1.5.) Aim(of(the(research((section(1.4) The#overall#aim#of#the#research#is#to#explore#how#the#adoption#of#more#energy#efficient#behaviours#at#home#could#be# encouraged.#Chapter#2#aims#to#provide#an#overview#of#the#nature#of#energy#use#at#home#and#the#factors#that#influence#energy# use#with#Chapter#6#investigating#whether#the#same#set#of#factors#and#conditions#can#be#found#within#the#empirical#study#in# Portugal.#Chapter#3#aims#to#better#understand#the#motivating,#enabling#and#reinforcing#factors#that#could#promote#the#adoption# of#energy#efficient#habitual#behaviours#and#practices#at#a#household#level,#while#Chapter#7#examines#if#similar#conditions#can#be# found#in#the#Portuguese#context.#Chapter#4#explores#the#potential#effectiveness#of#change#interventions#within#the#field#of# energy#use#at#home#and#the#different#types#of#interventions#that#might#be#used#and#subsequently#within#Chapter#8#how#those# are#perceived#and#evaluated#within#the#examples#of#practice#in#Portugal.#
  • 31. 1. Introduction 11 1.7 The research within the Portuguese context Previous research shows that structural psychological interventions can be applied to support and enable behavioural change of energy use at home, (Poortinga et al., 2004; Steg, 2003), and that such interventions have been employed with varying degrees of success, (Abrahamse et al., 2005; Geller, Harrington, Rosenfeld, Tanishima, & Unander, 2006; Heiskanen, Mourik, Feenstra, & Pariag, 2009; Kurz, 2002; Lutzenhiser, 2002; Southerton et al., 2011). Despite the growing body of existing research and evidence, there appears to be however a lack of clear evidence within the literature on the potential long-term effectiveness of such interventions. This is in particular true for studies carried out in Portugal. This lack in existing studies within Portugal perhaps results from the fact that energy consumption has only recently become a matter that gained in importance. It thus remains unclear whether the same set of factors and conditions from such existing studies can also be found within Portugal, and in the case that they could be found how effective such interventions have been in the long-term. Having remained relatively unchanged during the period from 2003 to 2008, the gross inland consumption of energy in Portugal decreased by 5.7 % in 2009, and much of this change is claimed to not be a result of a structural shift in the pattern of energy consumption, but that it can be attributed to a lower level of economic activity as a result of the financial and economic crisis, (Eurostat, 2015). Consumption rebounded in 2010 in most of the Member States — with only Lithuania, Greece, Portugal, Cyprus, Croatia and Spain recording consecutive contractions in consumption in 2009 and 2010 — possibly reflecting the low level of economic output and consumer confidence in several of these Member States, (Eurostat, 2015). Since 2012 this situation did change however and largely impacted by EU wide regulations and initiatives, (Portuguese Government, 2013). As a result of this the National Energy Efficiency Action Plan (NEEAP) has been adopted in 2008, and the National Renewable Energy Action Plan (NREAP) in 2010, (Portuguese Government, 2013). NEEAP and NREAP are both policy instruments aimed at achieving the targets and international commitments with regard to energy efficiency and the use of energy from renewable sources that the Portuguese Government had agreed to. NEEAP and NREAP are part of a policy that promotes a rational and sustainable energy model, without compromising the competitiveness of enterprises or the quality of life, programs and plans that annually provide strategic guidelines which aim to contribute to
  • 32. 1. Introduction 12 specific objectives and to allow to boost measures at all levels (ADENE, n.d.). NEEAP and NREAP also aim at identifying existing barriers, to support improvement of energy efficiency, increase in energy derived from renewable sources and with a view to establishing the most suitable programmes and measures for complying with the said commitments, without neglecting national situation, (Portuguese Government, 2013). Based on NEEAP and NREAP policy instruments the Regulatory Authority for Energy Services (ERSE), that is responsible for the definition of mechanisms to promote energy efficiency, has established a competitive mechanism to support actions for demand management within the ‘Plan to the Promotion of Efficiency in Electric Energy Consumption’ (PPEC) program. PPEC aims to promote measures to improve efficiency in energy consumption through actions undertaken by suppliers, network operators and promotion entities, and that are targeted at a number of market segments, (Portuguese Government, 2013). Such measures are divided in tangible and intangible measures and according to the following three market segments: industry and agriculture; trade and services; and the residential sector. Within the tangible measures there appeared to be a predominance of lighting measures (including public lighting), consumption management systems, or for electronic variable speed drives, (ERSE, 2010). Within the intangible type of measures the most common measures related to the dissemination and information campaigns targeted at a household level and at final consumers, but also to energy audits, (ERSE, 2010). The interest in the funding available has been growing over the years with the 2008 call for projects receiving 131 projects that were presented by 21 promoters and equalling a total amount of approximately 56 million euros of investment; and a final set of 159 projects presented by 48 promoters in 2011-2012 and equalling a total amount of approximately 57.1 million euros in funding, (ERSE, 2007; ERSE, 2009; ERSE, 2012). From this initial set, a selection process had to take place and for instance, in 2011, 57 measures were approved and received funding within the national context. Among those, 17 projects were implemented, in the market segment ‘Domestic Energy’ on three different settings: lighting (5), consumption management (9), and dissemination (3), (ERSE, n.d.). Two practical examples of such measures are described in the following: a) ‘Save Electric Energy’: in 2008 the Portuguese Association for Consumer Protection (DECO) promoted a national campaign in order to provide information on the meaning of saving electric
  • 33. 1. Introduction 13 energy, in three different main areas: home, work, and school. For this purpose, teams made up of young graduates were formed – named “carbon brigades”, who acted throughout the country raising awareness by awarding promotional material (ERSE, 2008); b) ‘Guide for Energy Efficiency’: launched in 2012 by the Portuguese government, directly supported by the Portuguese Agency for the Energy (ADENE). This guide provided practical recommendations and awareness-raising information regarding how to better use electric devices on a rational and sustainable way, in diverse contexts such as while using household appliances, but also as a guide to support the introduction of the new European Union Energy Label (ADENE, 2013). Apart from few exceptions most of the intangible projects do not report on the amount of energy that could be saved as a result of the project and as such there is no indicator of the success and efficacy of the intervention. In addition to those programmes and measures, the Portuguese government, in collaboration with ADENE, implemented two practical support financing instruments: the Energy Efficiency Fund (FEE) and the Support Fund for Innovation (FAI). The FEE is a financial instrument that aims to fund programmes and measures under the NEEAP, to encourage energy efficiency for both enterprises and citizens, to support energy efficiency projects, and to promote behavioural change in this domain, through cross-oriented actions of energy efficiency in the areas of behaviour, taxation and incentives, and funding, (FEE, n.d.). The FAI supports innovation and technological development projects, technology demonstration projects in the areas of renewable energy and energy efficiency, investment projects in energy efficiency, and partnership building support services between Portuguese companies and the scientific and technological system, (FAI, n.d.). With this Portugal is determined to achieve the national energy efficiency general target for 2020 that aims to reduce primary energy use by 25%, along with a specific target for Public Administration of achieving a reduction of 30% (European Commission, n.d.). Portugal also aims to reduce the nation’s energy dependence and safeguard security of supplies, by promoting a balanced energy mix, including the use of energy from endogenous renewable sources (Portuguese Government, 2013). The energyprofiler study that supported parts of the empirical study presented in this thesis has been carried out within exactly this wider context. The energyprofiler study was a collaborative Portuguese
  • 34. 1. Introduction 14 national funded research project coordinated by the author of this research on behalf of Energaia, a local energy agency in Vila Nova de Gaia, Portugal, together with two additional project partners, Factor Social and Terrasystemics. The study was one of the intangible PPEC measures selected in the 2009 application round and aimed at defining and characterizing the Portuguese population in segments/profiles based on the collected data regarding individual perceptions, attitudes, competence and patterns of energy consumption in the residential sector (Energaia, 2008). These segments/profiles could later be used to support the development of more specific and targeted policies and interventions in order to improve their efficacy towards reducing energy use at home. The motivation for the project was an identified gap in the knowledge regarding national energy use patterns in the residential sector in Portugal, and the energy saving potential that could be derived from such consumption patterns (Energyprofiler, 2011). The energyprofiler study thus attempted to explain what influences energy use at home and how could the population be segmented, highlighting the major differences in between segments, (Energyprofiler, 2011). Chapter 9 will provide further information on how the findings of the research presented in this thesis do relate to the national context as has been described within this section.
  • 35. 2. Energy use and sustainability 15 2 Energy use and sustainability This first, of three, literature review chapters provides a brief introduction to the subject of sustainability and energy use in the home. It explores the literature on sustainability aspects and the characteristics and determinants of domestic energy use and how lifestyles shape energy use, or negatively impact the sustainable use of it. Energy is essential for us to live the way we know. Even though improvements in efficiency could have allowed OECD 1 countries to decouple GDP growth from growth in primary energy consumption, (Geller et al., 2006), this has not happened and energy consumption is thus still closely linked to GDP growth, (Sorrell, 2007). This section will provide an overview on energy consumption, the variables that are influencing energy consumption and opportunities for greater efficiencies within European households in general, and Portugal in particular. Chapter 3 further explores what could explain energy use at home, with a particular focus on motivations and barriers towards the adoption of more energy efficient behaviours. The final literature review, chapter 4, explores how the adoption of more energy efficient behaviours could be potentially encouraged. 2.1 Domestic energy use The amount of energy consumed by individuals within their homes accounts for a significant share of total energy consumption 2 and CO2 emissions, (BPIE, 2011; Deutsch, 2010; Gardner & Stern, 2002). In 2009, European households were responsible for 68 percent of the total final energy use in buildings and 25.4 percent of total final energy was consumed by the residential sector in Europe in 2008, (EEA, 2011; Eurostat, 2011). Furthermore, in 2008 the residential sector accounted for 27 percent of the end-use greenhouse gas emissions from energy use in the EU-27 and in the case of Portugal, 16 percent, (EEA, 2011). In residential buildings most of the energy used is required for domestic hot water and space heating, ventilation, lighting and cooling, with home appliances accounting for approximately one-third of electricity used, (European Commission, 2010). Space heating is still the most energy intensive end-use in 1 OECD = Organisation for Economic Co-operation and Development 2 Total energy consumption and final energy consumption as defined in, (European Environment Agency [EEA], 2004, 2011; Official Statistics of Finland [OSF], 2013).
  • 36. 2. Energy use and sustainability 16 EU homes and accounts for around 70 percent of the total final energy use, though it has been decreasing in comparison to other sources in recent times, (Backhaus et al., 2012; BPIE, 2011). Energy consumption for water heating, for example, remained unchanged, whereas consumption for electrical appliances and lighting increased, (Backhaus et al., 2012; BPIE, 2011). Overall, energy consumption in the household sector continued to rise annually, though with a slower growth rate during the last few years, (European Environment Agency [EEA], 2008; Odyssee & MURE, 2011), which suggests that households have become, on average, more energy efficient, either deliberately or due to the economic downturn. From a geographical perspective a difference appears to exist between northern and southern European countries, with heating needs in southern countries, such as Portugal, being lower due to milder winters, (Healy, 2004; WHO, 2012). Southern countries however have a high ‘relative’ energy consumption rate for two identified reasons: firstly the lack of sufficient thermal envelope insulation 3 in southern European building stock, and secondly the fact that cooling becomes an important contributor to overall consumption where homes are, in many cases, equipped with air conditioning systems, (BPIE, 2011). For Portugal the residential sector similarly shows rising energy demands, which increased from 2.510 kWh/household in 2008, to 2.630 kWh/household in 2009 and to 2.671 kW in 2010, (DGEG, 2010). A more in-depth analysis of the latest data, (INE, 2011; INE I.P./DGEG, 2011) 4 , on household energy consumption in Portugal and as depicted within Figure 2-1, shows that electricity emerged as the main source of energy consumed in households, excluding fuels used in vehicles, representing 42.6 percent of total energy consumption. Electricity was mainly consumed in kitchen and electrical appliances, amounting to 41 percent and 33 percent of the overall electricity consumption respectively. 3 Insulation of roof, exterior walls and floor. 4 Data report over the reference period from October 2009 to September 2010 unless otherwise stated.
  • 37. 2. Energy use and sustainability 17 Figure 2-1: Distribution of energy consumption in households by source type in 2010, (INE, 2011; INE I.P./DGEG, 2011). Electricity consumption has seen the highest increase from 15.8 percent in 1989, to 27.5 percent in 1996 and now towards 42.6 percent, with electricity now being present in 99.9 percent of the households. At a European level, (European Commission, 2010), there has been an increase in the overall available income and therefore thermal comfort, as well as a growing number of electrical appliances within households that will have contributed to an overall increase in energy consumption, (DGGE/IP-3E, 2004; INE, 2011; INE I.P./DGEG, 2011). Firewood is used in 40 percent of households and emerged as the second main source of energy consumed in Portuguese households, with a weight of 24.2 percent in the total energy consumed by the domestic sector. This energy source has been losing importance in the past few years, decreasing from 60.3 percent in 1989, to 41.9 percent in 1996 and is mainly used for house heating and in the kitchen, (INE, 2011; INE I.P./DGEG, 2011). This predominance of firewood and electricity as the main energy sources might be related to the recent introduction and consolidation of the gas network. Further to this, almost 85 percent of the energy within households is being used in three main categories as mapped in Figure 2-2: kitchen, (39 percent), water heating, (23.5 percent) and house heating, (21.5 percent) 5 , (INE, 2011; INE I.P./DGEG, 2011). House heating thus has a lower share of total energy consumption compared to European values that shows 70 percent on an average, (Backhaus et al., 2012; BPIE, 2011). 5 Within the kitchen, energy would be spent on preparing food and refrigeration, but also on activities such as laundry or dishwashing, with a predominance of energy intensive home appliances. Water heating is mainly for showering and accounts for almost ¼ of the energy being consumed at the household, (INE I.P./DGEG, 2011). 42,6% 24,2% 13,6% 3,0% 9,0% 2,4% 4,3% 0,7% 0,2% Distribution of energy by source type Electricity Firewood LPG botlles (butane) LPG botlles (propane) Natural Gas Piped LPG Heating oil Solar thermal Coal
  • 38. 2. Energy use and sustainability 18 Figure 2-2: Distribution of energy consumption in households by use type in 2010, (INE I.P./DGEG, 2011). Average energy usage per Portuguese household is increasing and is perhaps a result of an increase in average income, which is known to influence the amount of perceived individual needs, (WWF, 2012). As can be seen from the data presented in this section, households hold a significant potential for cost effective savings that could be realized through structural and policy measures. Improving building requirements or retrofitting opportunities thus hold a great potential for reducing energy consumption. 2.1.1 Invisibility of energy use One distinct characteristic of energy consumption and in comparison to the consumption of physical goods, is its “Invisibility”, (Darby, 2006), or “Doubly invisibility”, (Burgess & Nye, 2008). Energy is not used directly at home, but is rather mediated by the appliances people have and practices people do at home. For example, people do not simply consume gas or electricity, but rather the services these energy sources provide, such as cooking, lighting, or washing, (Martiskainen, 2007). As such, energy might be an abstract concept and it might be difficult to account for its use, or, environmental impact. This distinctive characteristic might therefore pose an additional barrier towards promoting more energy efficient lifestyles and poses the question as to whether improving energy visibility could be a way to reduce energy use. Research suggests this might be the case, or at least partially so. For the case of using information and feedback provisioning, as a means to make energy use visible, studies found that this had resulted in less energy use at home, though it appeared to be not enough to promote long-term change, nor were the realized savings seen as being significant with regards to achieving sustainable energy use levels, (Abrahamse et al., 2005; Geller, 2002; Martiskainen, 2007; Staats, Wit, & Midden, 1996). As shown from the 21,5% 0,5% 23,5% 39,1% 10,9% 4,5% Distribution of energy by use type House heating House cooling Water heating Kitchen Small domestic appliances, entertainment and computer equipment Lighting
  • 39. 2. Energy use and sustainability 19 literature, energy can become visible at certain circumstances, for instance, through energy bills, (Brandon & Lewis, 1999; Darby, 2006), through the services and amenities that energy provides, (Goldblatt, 2005; Martiskainen, 2007), or when purchasing a new home appliance, (Gardner & Stern, 2002, 2008; Jackson, 2005). This poses the question as to whether energy becoming more visible could be a way to encourage the adoption of more energy efficient behaviours. 2.1.2 Energy use and energy saving at home It is a truism that buildings do not use energy, but people do, even though people do not actually explicitly want to use energy; it is services like light and comfort they really seek, (Janda, 2011). Currently the focus on intervention requires not only the use of less energy, (‘negawatts’), but also more efficient use. An example of the former could be to switch lights off when leaving a room and the latter could be to change to more energy efficient light bulbs in order to provide lighting in a more efficient way. Energy saving behaviours can be distinguished between efficiency and curtailment behaviours. Efficiency behaviours are infrequent, one-off type of behaviours, which often entail an investment, such as loft or cavity wall insulation, or buying an energy efficient air conditioner, (Abrahamse et al., 2005; Gardner & Stern, 2002; Kempton et al., 1992). Curtailment behaviours in contrary are those that must be performed frequently, involving repetitive efforts to reduce energy and involve more operational day to day habits and routines, such as lowering the thermostat and turning lights and appliances off, (Abrahamse et al., 2005; Gardner & Stern, 2002; Kempton et al., 1992). Each of these two groups requires different levels of investment in time, money or individual effort and commitment to perform. For example, to insulate one’s loft requires the time to look for an adequate supplier, to hire someone to perform the work and demands a certain amount of investment; but it would be a one-off action. On the other hand, to maintain a lower thermostat setting, (even if one has a properly insulated loft), requires a certain level of knowledge, willingness and commitment not to increase room temperature on a day-to-day basis; this is not a one-off action, but a frequently performed one, a so-called routine behaviour. Less unanimous agreement, than on the grouping of these two behaviours, can be found in the impact they can have in terms of energy saving and conservation, and there is some disagreement as to whether curtailment or efficiency behaviours are more effective in reducing energy use at home, (Martiskainen,
  • 40. 2. Energy use and sustainability 20 2007). Some studies suggest that curtailment behaviours could initiate sustainable, long-term behavioural changes, (Geller, 2002), while others suggest that efficiency behaviours are generally more effective in obtaining actual energy savings, (Abrahamse et al., 2005; Gardner & Stern, 2008). In addition to this, curtailment behaviours might be perceived, by individuals, as negligible behaviours when it comes to energy savings, as individually they would generate only small savings and therefore, in order to produce an impact would require adoption by many people, (Winter & Koger, 2004,) and/or the adoption of a number of behaviours by each individual. 2.2 Determinants of energy use at home The way people use energy in the home is the result of a mixture of socio-economical-techno-cultural factors that frames needs, opportunities, belief systems and abilities, as illustrated in Figure 2-3. Figure 2-3: Main factors influencing consumer behaviour and emergence of consumption practices, (EEA, 2013). Energy use at home is often explained as based on a set of enabling variables and existing conditions. For instance, the European Environment Agency, (EEA, 2013), suggested a number of factors influencing consumer behaviours and emerging practices that could support the understanding of energy use at home, as well as the adoption of more energy efficient behaviours. This section will discuss determinants that had been identified from the literature as influencing energy use at home, namely, social and cultural influences, comfort, convenience and needs, norms; technological developments; as well as economic and demographic trends, (Abrahamse et al., 2005; BPIE, 2011; DGGE/IP-3E, 2004; Goldblatt, 2005; INE I.P./DGEG, 2011; Lomas, 2010; Spaargaren & van Vliet, 2000; Wilhite & Lutzenhiser, 1999) and that can be of an internal, external, social, or structural nature, (Abrahamse et al., 2005; Gardner & Stern, 2002;
  • 41. 2. Energy use and sustainability 21 Kempton, Reynolds, Fels, & Hull, 1992; Martiskainen, 2007; Nye et al., 2010; Prendergrast et al., 2008). The work of Jackson (2005) shows for example that internal determinants might consist of attitudes, beliefs and norms, while external determinants could constitute regulations. Abrahamse et al. (2005) in contrast shows that determinants might include wider societal, as well as personal factors, while the work of Dholakia and Dholakia (1983) shows that determinants could result from a series of nested and interlocking choices, in which macro-choices delimit and define the scope of micro-choices and where household energy use is seen to be as not only the result of a choice among behavioural alternatives but where the production of such alternatives is also viewed as the result of a social choice process. Thus there appears to be a diversity of macro- and micro- factors. Macro-level factors such as technological development, economic growth, demographic factors, institutional factors and cultural development appear to influence behaviour at the broader level, while micro-level factors such as motivation, opportunity and ability appear to shape behaviour at the individual level, (Darnton, 2008; Jackson, 2005; Nye et al., 2010; Prendergrast et al., 2008; Stern, 2000). Thus energy use is determined by multiple conscious and unconscious processes, driven by internal psychological variables, such as norms, beliefs or values, as well as external variables, (e.g. social, economic physical), drivers and constraints, personal capabilities, or habits and routines, (Jackson, 2005; Nye et al., 2010; Stern, 2000). As such energy consumption is not a behaviour in itself, but rather a consequence of particular behaviours, (Becker, Seligman, Fazio, & Darley, 1981). Consequently to understand and influence behaviours on energy use would require, firstly, an understanding of the determinants of energy use behaviours. 2.2.1 Social and cultural influences Social and cultural factors, such as thermal comfort, cleanliness and convenience in the home, or ambient lighting that impact the amount of energy used at home are influenced both by individual preferences and common social understandings, (Giddens, 1984; Lewis, 1969). As an example, for Portugal the penetration rate of refrigerators, washing machines and televisions at home has increased to close to 100 percent, suggesting that owning these appliances is now considered to be a standard, (INE, 2012). This introduction of home appliances brings along social practices that evolve over time and develop into social norms that establish standards that can lock individuals into what is considered to be a ‘normal’ practice. This can lead to individuals finding it hard to change their domestic routines and behaviours, or to change them in a way
  • 42. 2. Energy use and sustainability 22 that would bring about a significant impact in terms of energy use, (Goldblatt, 2005; Maréchal, 2010; Shove, 2004). This understanding of behaviour as an outcome of routinized, socially learned habits or practices, embedded into particular socio-technical infrastructures, or a system of provision, can be traced to sociology and to the on-going debate about structure vs. agency; which defines the relationships between individuals, communities and society in more detail. If on the one hand, human behaviour is constrained by structural factors, on the other, social structure is a human product of itself. This is to say that established rules and ways of doing things can be changed once people start to ignore them, replace them, or reproduce them differently and as a result develop a new social practice, (Giddens, 1984). There are, however, limits as to how much individuals can change social structure, (Heiskanen et al., 2009). This relates to the debate around whether consumers are free to make choices about their own actions, or whether forces outside their control impose those, (Giddens, 1984). Giddens’ work (1984), for example has been setting the ground for viewing consumption as a set of social practices that are influenced on the one hand by social norms and lifestyle choices, and on the other, by the institutions and structures of society, as exemplified in Figure 2-4, (Giddens, 1984; Randles, 2009; Spaargaren and van Vliet, 2000). Figure 2-4: An Actor-Structure Model of Consumption, (adapted from Spaargaren and van Vliet (2000)). The model in Figure 2-4 shows the interplay of social norms, lifestyle choices and the institutions and structures of society, which comprise the two basic pillars of sociological theory. The model suggests that
  • 43. 2. Energy use and sustainability 23 shifting consumption patterns requires ‘raising’ routine behaviours from a level of practical consciousness 6 to discursive consciousness 7 , therefore making them more visible. This distinction can be of relevance since most of the everyday, routine actions that consume energy at home are performed in practical consciousness, (Spaargaren & van Vliet, 2000), reminiscent of being under automatic pilot control that appears to lock-in individuals. 2.2.2 Comfort, convenience and needs In today’s developed economies socially perceived needs frequently relate to comfort, convenience and wellbeing, and are perceived as being part of a ‘normal’ lifestyle which needs to be satisfied, (Lehman & Geller, 2004; WWF, 2012). Comfort and convenience needs are the result of technological progress, increased income levels, availability of labour saving appliances and cultural/social dynamics, creating new practices that embed into the social fabrics of daily lives, (Shove, 2009). Examples of this are the automation of jobs previously done by hand, and substituting energy-using appliances like computers and consoles where in the past people would have worked using pen and paper, or entertained themselves with board games or books. Comfort conditions, in general, are socially influenced and may change with time as design, activity, and technology change, (Shove 2003). The gap between estimated and actual energy performance in housing tends to directly increase to increasing comfort levels beyond what was predicted, (Stevensen and Rijal, 2010). One such examples can be seen in the increasing penetration of central heating and cooling systems of the last few years that seems to be accompanied by a growing, perceived need of improving indoor thermal comfort, (Eurostat, 2007). 2.2.3 Norms and energy efficiency Norms are rules and standards that impact energy use as they guide and/or constrain social behaviour, (Cialdini & Trost, 1998). Within the literature a number of different norms are defined, such as personal and moral norms, (Schwartz, 1970, 1977), subjective norms, (Ajzen & Fishbein, 1980) and descriptive and 6 Practical consciousness consists of all things which actors know tacitly about how to ‘go on’ in the contexts of social life without being able to give them discursive expression (…) describing behaviours that reside in the ‘non-consciousness (Giddens, 1984). 7 Discursive consciousness can manifest in purposeful and intentional behaviour, (Giddens, 1984).
  • 44. 2. Energy use and sustainability 24 injunctive norms, (Cialdini et al., 1991; Cialdini et al., 1990). Norms might emerge from interaction with others, they may or may not be stated explicitly and sanctions for deviating from norms are, mostly, imposed by social networks, not the legal system, (Cialdini & Trost, 1998). Norms further tend to motivate and constrain individual actions by promising social rewards and sanctions for acting, or not acting, in certain kinds of ways. For instance, one might not litter not only because one might get a fine, but also because one does not want others to think, “I’m the kind of person that litters”. Individuals tend to negotiate and inform much of their behaviour on the basis of what others do around them and by simply copying the way others around them behave. This is used as a means to bypassing the mental effort involved in thinking it out for oneself and/or to free up cognitive resources for more, perceived, important tasks, (Cialdini et al., 1990). Whether and how one responds to a norm also depends on which kind of norm is salient for that specific circumstance, (Cialdini, 1993; Cialdini et al., 1991; Cialdini et al., 1990; Steg, 2003). Within this structure, norms influence behaviour through imitation, social comparison, or social learning theory, (Bandura, 1977b, 1986; Cialdini et al., 1991). For the theoretical relation between norms and environmental significant behaviours 8 , an ample body of available literature exists, (Abrahamse et al., 2005; de Groot, Steg, & Dicke, 2007; Guagnano, 2001; Osterhus, 1997; Schultz et al., 2005), but less evidence can be found within the literature for the contribution of norms to encourage the adoption of more energy efficient behaviours. Currently, the socially accepted norm appears to be towards the acceptance of an over-consumption of energy and thus adopting more energy efficient behaviours will be difficult to achieve without such behaviours being viewed as the social norm, (Schwartz, 1977; Stern, 1999, 2000). In addition to this, the growing number of needs as well as owned home appliances might be seen as an indicator of the social norm moving towards a higher level of consumption, (Cialdini et al., 1990, 1991; Triandis, 1977). Norms further appear to impact behaviour differently. This is to say that personal norms and attitudes that are based on altruistic and biospheric/ecological values seem to be more effective at leading to simple, repetitive, low-cost, (effort, money, and time), energy saving behaviours, (Black, Stern, & Elworth, 1985; Heberlein & Warriner, 1983; 8 Environmentally significant behaviour is behaviour that does not “threaten human health, welfare, or other things people value”, (Stern, 1997, p. 15) and that is characterized by its “positive impact on the availability of materials or energy from the environment and/or by the extent to which the behaviours positively alter the structure and dynamics of ecosystems or the biosphere”, (Stern, 2000, p. 408).
  • 45. 2. Energy use and sustainability 25 Stern, 1992). Specifically, research indicates that altruistic/social norms are much more strongly related to, “low constraint”, environmentally friendly behaviours, such as adjusting a thermostat, than they are to, “high constraint”, behaviours, such as major capital investments to improve the energy efficiency of one’s home, (Black et al., 1985; Lindenberg & Steg, 2007). For example, an intention to reduce car use may be seen as a more costly behaviour compared to buying organic food because of the, perceived, higher inconvenience associated with reducing car use, (Abrahamse et al., 2005; Poortinga et al., 2004). 2.2.4 Economic influences Economics and its, “Rational man”, principle, (Mill, 1836), suggest that people are driven by self-economic interest, i.e. people will maximize their set of preferences and their utility, (i.e. the value attached to an outcome). In a period of rising energy prices, (Odyssee & MURE, 2011) and in accordance to the, “Rational man”, approach, reducing energy bills should thus be a primary motivation for saving energy. This is to say, one would expect energy use to fall once prices go up, in order to not increase the percentage of income dedicated to energy. However, evidence suggests that the relation between price and energy use is not 1 to 1, meaning, for instance, a 10 percent increase in price does not lead to a 10 percent decrease in energy use. This phenomenon is known within the economics literature as, ‘price elasticity’, i.e. the percentage change in one variable following a percentage change in another, holding other variables constant, (Sorrell, 2007). Demand for energy is often perceived to be, ‘inelastic’, in the short term, i.e. energy use does not change straight away when prices increase. But, it is seen to be, ‘elastic’, in the long term, i.e. a few years after price increases households are able to modify to save energy. This is to say that in the short term, rising prices might not be effective in significantly stimulating demand reduction. This is in the uptake of demand reduction measures that could save energy at home, (Department of Energy & Climate Change [DECC], 2011). An analysis of US demand elasticity in response to price rises suggests that a ten per cent increase in electricity prices only decreases demand by around one per cent, (Nakajima & Hamori, 2010). Elasticity might be one of the reasons why higher energy prices, government taxes and subsidies have apparently not had the expected impact in reducing energy consumption at a household level, (Spaargaren & van Vliet; 2000).
  • 46. 2. Energy use and sustainability 26 2.2.5 Income levels and energy poverty In the case of income levels, the literature provides some apparent contradictory findings. Evidence has equally shown that higher income levels often relate to higher energy use, (DECC, 2011), as well as for apparent dissociation, with similar income level households using significantly different levels of energy, (Gatersleben et al., 2002). If indeed energy use increases with income level, then one could expect more affluent households to use more energy than less affluent ones. However, poorer households are also more likely to live in poorly-insulated homes and less likely to be able to improve their homes’ energy efficiency, (Scottish Government, 2010). For instance, for those in fuel poverty, they might not be able to afford to spend more on energy and are forced into using less energy if prices rise. Conversely, wealthier households may be more prone to ignoring ‘avoidable’ energy use, such as heating unused rooms, or leaving unnecessary lights on. With this the demand for energy tends to be more elastic in poorer households than in wealthier ones, meaning that they tend to use less energy if prices rise. Further to this, poorer households might also experience energy poverty, which is a situation where a household is unable to access a socially- and materially-necessitated level of energy service in the home, (Buzar, 2007a). According to Boardman (1991, 2010), a household is said to be in fuel poverty if it needs to spend more than 10 percent of its (disposable), income on household fuel, (energy), including heating the house to acceptable World Health Organization levels 9 . According to the literature, fuel poverty results from a combination of low income, low energy performance dwellings and increasing energy prices, (UK Government, 2013) and there is equally evidence that southern Europe suffers from the highest levels of fuel poverty and the poorest housing conditions within the EU, (Healy, 2003; SEI, 2003). The inability to afford to heat the home adequately is particularly pronounced across eastern and southern European states, with over 30 per cent of households in Portugal, Bulgaria and Cyprus declaring this inability, (The University of York, n.d.). Magalhães and Leal (2012) estimate a 92 percent fuel poverty rate for mainland Portugal under nominal conditions by considering a tariff of 0.089€ per kWh of energy supplied. Healy (2004) reported that in Portugal only 6 percent had cavity wall insulation, 3 percent double-glazing, 2 percent floor insulation and 6 percent roof insulation in their homes, (one of the usual pre-conditions for fuel poverty). In addition to this, 9 The World Health Organisation takes 21ºC as a benchmark temperature for those more vulnerable, such as the elderly and handicapped and a minimum temperature of 16ºC for able-bodied, healthy people, but recommends a minimum of 18ºC for sedentary activities.
  • 47. 2. Energy use and sustainability 27 nearly a quarter of Portuguese households stated that they had rotten window frames, while a third revealed that they had patches of condensation on indoor walls, two good indicators of poor energy efficiency, (Healy, 2004). Further to this, 19 percent of households in Portugal were suffering from leaking roofs, indicating the absence of adequate roof insulation, (Healy, 2004) and the latest data for Portugal reveals that 26.8 percent reported their inability to keep their home adequately warm, (Eurostat, 2013). An additional problem in Mediterranean states is the need for cooling, with 30 percent of the population in the 8 states bordering the Mediterranean Sea reporting that they are unable to keep their homes adequately cool in summer, (SILC, 2007). Even though heating seems still to be the main issue in the short term, cooling is likely to become an increasingly important issue over the coming years, in particular with rising global temperatures, (ECI, 2005). The limited extent of certain types of networked energy infrastructures, (particularly gas), means that in addition to inefficient residential stocks and affordability issues, energy deprivation is also predicated upon the spatial and technical limitations associated with switching towards more affordable fuel sources in the home, (Buzar, 2007a, 2007b, 2007c). Besides decreasing the quality of life and influencing social fulfilment, there is also a strong associations between inadequately heated homes and increased rates of morbidity and mortality, (Harrington et al., 2005). The fact that in Portugal, the excess of winter mortality rates and hospital episodes compared to that of summer is among the highest in Europe, adds to the suspicion that households are not heating their homes adequately and to an association with mortality rates and hospital episodes, (Eurowinter Group, 1997; Gascoigne, Morgan, Gross, & Goodwin, 2010; Healy, 2004; IPCC, 2007; McMichael, Woodruff, & Hales, 2006). 2.2.6 Demographic trends In addition to economic influences, there are two demographic trends that have been observed over the last few decades that seem to influence energy use: household size and composition. Today people in industrialised countries tend to live in larger houses, with a lower, average number of occupants per household and a growing number of single-occupancy dwellings, (Goldblatt, 2005). A larger home implies increased floor and air space to heat, or cool and thus an increase in the required energy to maintain a comfortable temperature in the house. Evidence suggests that the more people there are in a household
  • 48. 2. Energy use and sustainability 28 the more energy efficient per capita that household becomes, meaning that single-person households tend to use more energy per person when compared to multi-person households, (Energy Saving Trust, 2012). As a result of this, projected population growth might be less important than the average number of occupants per household and in particular, the number of single occupancy dwellings. 2.2.7 The role of infrastructure and technological factors in influencing energy use at home During the past few decades there has been an extraordinary growth in the number and choices of consumer energy-using products, (Energy Saving Trust, 2011). This is in particular true for labour saving devices and personal/home entertainment systems, with the associated energy consumption contributing to a continuing upward trend in domestic electricity consumption, (Energy Saving Trust, 2011). Further to this, technologies that are designed to ‘improve’ people’s lives, such as air-conditioning, have rapidly developed from being a luxury towards becoming essentials, (Shove, 2003). Despite improvements in energy efficiency in homes and products, the demand for energy has outstripped this improvement, (Energy Saving Trust, 2011; Odyssee & MURE, 2011). This suggests that even though technological developments increased the energy efficiency of appliances, part of this efficiency gain is being, taken back (Odyssee & MURE, 2011). This, take back, could be one explanation for the difference between, actual energy efficiency and potential efficiency, also known as the energy efficiency gap, (Feenstra et al., 2009). Overall four reasons seem to contribute to ‘take back’. Firstly, due to the growing number of energy using appliances to be found in the average home, (Energy Saving Trust, 2011). Secondly, the way these appliances are used, (Energy Saving Trust, 2011; Goldblatt, 2005; INE I.P./DGEG, 2011; Lomas, 2010). Thirdly, within the socio- technical system and the way that individual choices are constrained and shaped, the so-called behavioural lock-in, (Energy Saving Trust, 2011; Direção Geral de Energia e Geologia [DGEG], 2010; Maréchal, 2010; Quercus, 2008). The fourth reason relates to the, ‘rebound effect’, where energy efficiency improvements may impact on the demand for other goods and services, as the savings from one appliance can be used on other energy using activities, (Binswanger, 2001; Khazzoom, 1980; Odyssee & MURE, 2011; Sorrell, 2007). However technological developments are not limited to appliances but also to the building characteristics. Energy use at home is influenced by building characteristics such as age, orientation, size, building envelope (i.e. roof, exterior walls, and floor) and the performance of installed heating/cooling system, (BPIE, 2011;
  • 49. 2. Energy use and sustainability 29 DGGE/IP-3E, 2004; Goldblatt, 2005). The characteristics of a building, its design and its technical standards do not only influence well-being, but they also define how much energy is consumed in and by a building, and as a consequence, how much heating, ventilation and cooling energy is needed to create a comfortable environment based on respective climate conditions, (BPIE, 2011). Significant savings in energy use could be achieved by improving building characteristics and the European Union has been active in this area and has passed a number of European Directives, (Energy Performance of Buildings Directive - EPBD), so as to define the minimum standards to be used in new buildings, as well as within the refurbishment of existing buildings. However, since buildings have a long service life, this may not deliver immediate energy savings, or at least not to the level that might be required. Even though ‘new’ buildings are expected to consume around ¼ less than the ones built in 1990, they accounted for only 21 percent of total building stock in Europe, thus the impact of more energy efficient ways of building will take time to produce global results, (BPIE, 2011; Odyssee & MURE, 2011). This is to say that people might be temporally locked into the buildings they live in, (Maréchal, 2010) and that it will require time to increase the energy efficiency of the buildings and to reduce the amount of energy being used. The same long-term dilemma can be seen in the heating/cooling systems of buildings that equally have a relatively long lifetime, which in the case of standard boilers is normally 15-20 years, (Energy Saving Trust, 2011). For this particular case and due to low substitution rates, effort might rather be focused on the effective use of heating/cooling systems, rather than on the substitution, which requires investment, (Energy Saving Trust, 2011). 2.2.8 The rebound effect and its influence on determining energy use at home The potential, energy savings, from improved energy efficiency are commonly estimated using basic physical principles and engineering models. However, the savings that are realized in practice generally fall short of these engineering estimates. One explanation for this is that improvements in energy efficiency apparently encourage a greater use of the services, a response known as the energy efficiency, rebound effect, or, take-back effect, (Khazzoom, 1980). Generally speaking this rebound, or take-back effect is measured by the difference between the projected and actual savings due to increased efficiency and is normally expressed as a percentage of the expected energy savings from energy efficiency improvements; a ratio of the lost benefit compared to the expected environmental benefit, once consumption is constant,
  • 50. 2. Energy use and sustainability 30 (Grubb, 1990; Sorrell, 2007). Thus a rebound effect of 20 percent means that only 80 percent of the expected energy savings have been achieved. In accordance to Gottron (2001) and Sorrell (2007) three different types of rebound effect might be observed: • Direct rebound effect: energy efficiency improvements make energy services cheaper, so consumption of those services increase once the consumer chooses to use more of the resource instead of realizing the energy cost savings; e.g. people have their loft insulated and later raise their thermostat to a higher temperature. • Indirect rebound effects: even if consumption of energy services remains unchanged, the consumer can chose to spend the money saved by buying other goods, which use the same resource; e.g. individuals have their loft insulated or buy a fuel-efficient car and therefore realize savings on fuel bills, but then use those savings to later go on a long haul vacation. • Macroeconomic effects: any reductions in energy demand will translate into lower energy prices that encourage increased energy consumption. Decreased demand for a resource leads to a lower resource price, making new uses economically viable; e.g. new, more energy efficient technologies that make items, such as air conditioners more accessible and affordable to users. Direct and indirect rebound effects appear to vary widely depending on technologies, sectors and income groups and often they cannot be quantified with much confidence, (Sorrell, 2007). This appears to support on-going discussion and lack of agreement regarding size and impact of the rebound effect. On the one hand findings show that rebound effects could completely offset the energy savings from improved energy efficiency, (Brookes, 2000; Guertin, Kumbhakar, & Duraiappah, 2003; Herring, 2006; Sorrell, 2007). Recent research has shown take-back examples where thermal efficiency improvements were out-weighed by increases in energy levels for lights and appliances, (Lomas, 2010; Wright, 2008). On the other hand, findings indicate that the rebound effect is of minor importance, largely due to the understanding that demand for those services appears to be inelastic in most cases, as energy cost represent only a small share of the total costs of those services, (Lovins, 1998; Lovins, Henly, Ruderman, & Levine, 1988; Schipper & Grubb, 2000). Even some of the researchers that argue towards the impact of the rebound effect acknowledge that for specific energy services, complete offset could decline as demand saturates, (Sorrell,
  • 51. 2. Energy use and sustainability 31 2007). As such, reducing energy use at home by improved technological solutions might be insufficient without the cooperation of individuals, since the use of energy at home results from a complex interaction between built form, location, energy-using appliances, occupants and the affordability of fuel, (Crosbie & Baker, 2010). 2.3 Concluding remarks This chapter looked at characteristics, (RQ1a) and determinants, (RQ1b), of energy use, showing that there is a growing trend in energy use and a multitude of reasons that shape and influence energy use at home, (RQ2). A distinctive characteristic of energy use at home, (RQ1a), could be seen in its, ‘invisibility’, as a characteristic in itself, further expressed through energy entering homes through hidden pipes, or by the nature of current metering and billing systems, (Burgess & Nye, 2008; Darby, 2006; Hargreaves, 2012). Energy is not used directly at home but rather mediated by the appliances people have and the practices people do at home, such as cooking, lighting, or washing for example, (Martiskainen, 2007). A second key characteristic, (RQ1a), is the common understanding of energy being something essential for people to live in the way we know and that it is considered almost as a given that is normal to have, or at least to use the services and amenities that it provides, (Geller et al., 2006; Sorrell, 2007). With this, it could also be seen that energy might be an intermediary between our needs and the fulfilment of those needs. It also could be seen that there are numerous determinants that impact energy use that result from a mixture of socio-economical-techno-cultural factors that frame needs, opportunities, belief systems and abilities, as illustrated in Figure 2-3. With this, it could be seen that determinants of energy use, (RQ1b), are frequently a result of enabling variables and existing conditions where a number of factors influence the consumers’ behaviours and emerging practices, (EEA, 2013). Determinants that the literature provided include, (RQ1b), social and cultural influences, comfort, convenience and needs, norms, and technological developments, as well as economic and demographic trends, (Abrahamse et al., 2005; BPIE, 2011; DGGE/IP- 3E, 2004; Goldblatt, 2005; INE I.P./DGEG, 2011; Lomas, 2010; Spaargaren & van Vliet, 2000; Wilhite & Lutzenhiser, 1999). It could be seen, for example, that technological development in buildings and appliances allows for increased efficiency, though a growth in the number of such technologies equally
  • 52. 2. Energy use and sustainability 32 leads to an increase in energy demand and overall energy consumption, a situation commonly referred to as the rebound effect, (Energy Saving Trust, 2011; Khazzoom, 1980). It also could be seen that infrastructure-social-cultural settings can act in a way that locks people into their building infrastructure and behaviours, (Maréchal, 2010). In this regard research to date indicates that buildings hold great potential for energy saving, yet their service life and reduced refurbishment rates may require more time to support more energy efficient lifestyles, (BPIE, 2011; Odyssee & MURE, 2011). An overall increase in income levels, (Energy Saving Trust, 2011), needs, (Lehman & Geller, 2004), as well as an increasing number of single households, further increases total energy consumption, (Energy Saving Trust, 2012; Goldblatt, 2005). All of these factors are considered to contribute to an increase in energy use, or to the take back of efficiency improvements achieved during the past few years, (Odyssee & MURE, 2011), also known as the ‘energy efficiency gap’, (Feenstra et al., 2009). For southern European countries it can also be seen that the poor quality of the building envelope results in a less efficient use of energy in order to maintain the required level of thermal comfort, (Healy, 2003; SEI, 2003). With regards to how people perceive their energy use at home, (RQ1c), a number of different aspects could be found in the literature. It could be seen that people perceive their energy use as normal, even if as such it includes commodities that are indispensably necessary to support one’s life, but also those that are perceived as being ‘normal’, (Lehman & Geller, 2004; Smith, 1776; Townsend, 1979, WWF, 2012). The chapter further discusses that the understanding of what ‘normal’ is, is perhaps not normal at all, or normal for all and that ‘normal’ standards can be defined as a mix of individual preferences that are influenced by social common understandings, (Giddens, 1984; Lewis, 1969).
  • 53. 3. Energy use behaviours: motivations and barriers 33 3 Energy use behaviours: motivations and barriers This chapter explores the nature of energy related behaviours and investigates the underlying motivations and barriers that can encourage the adoption of more energy efficient ones (RQ2). 3.1 Motivations for saving energy at home Saving money or reducing cost is commonly reported as the primary motivation for saving energy at home, (Leiserowitz et al., 2009). Besides the financial motivation, other known motivational variables include, for example, the need to comply with social norms, or to comply with personal, altruistic and moral motivations such as environmental protection, (IPPR, 2009; Leiserowitz et al., 2009). Leiserowitz et al. (2009) found for example, that such personal, altruistic and moral motivation for Americans can be translated into actions such as to turn off the lights, lowering the thermostat in winter, or raising it in summer. In line with this, Brouwer et al. (2008) found that 80 percent of Europeans would pay, on average, an extra one Euro per 100 Kilometre for their airline ticket out of a sense of moral obligation and responsibility, with respect to climate change, concern for future generations and the environment. Yet, Kaplan (2000) found, for example, that personal, altruistic or moral motivations can also work in the opposite way and cause feelings of helplessness, or stressing the individual sacrifice and thus acting as a motivation to maintain existing energy related behaviours, with individuals resisting making changes that they perceive as reducing quality of life. 3.2 Pro-environmental concern: a motivational variable or barrier to behaviour? Research to date indicates that the majority of people in industrialized countries (1), are aware of environmental problems, (Diekmann & Meyer, 2008; Leiserowitz, 2007; Lorenzoni & Pidgeon, 2006; Poortinga, Pidgeon, & Lorenzoni, 2006) (2), hold positive attitudes towards environmental protection (3), are aware of the environmental consequences and personal risks and (4), hold information regarding ways
  • 54. 3. Energy use behaviours: motivations and barriers 34 on how to tackle the problems, (Brouwer, Brander, & van Beukering, 2008; Eurobarometer; 2011a, 2011b; Maibach, Roser-Renouf, & Leiserowitz, 2009; Whitmarsh, 2009). These findings together suggest that pro- environmental behaviour should be widespread among these populations, which however does not seem to be apparent. Despite such positive attitudes, concerns and awareness, these do not seem to translate adequately into pro-environmental behaviours and thus there appears to be an attitude-behaviour gap, (Kollmuss & Agyeman, 2002; Lehman & Geller, 2004; Tobler et al., 2012), with people not behaving in accordance to their attitudes and adopting pro-environmental and energy efficient behaviours at home. Looking at the literature it appears however, as if there are a number of reasons that might explain this apparent phenomenon. Firstly, environmental problems appear to be perceived as a less immediate threat within the limited capacity of individuals for worrying about an issue; a phenomenon known as the finite pool of worry, (Linville & Fischer, 1991). As the level of worry increases about one type of risk, concern about others may decrease, with people tending to pay more attention to near-term threats, such as the economic crisis, rather than to larger and long-term threats, such as climate change, (Leiserowitz, Maibach, Roser-Renouf, Smith, & Hmielowski, 2011; Linville & Fischer, 1991; Upham et al., 2009). Most recent data for Europe confirms, for example, that topics such as climate change have been losing importance, whilst at the same time, anxiety over the economy rose, (Eurobarometer, 2010; Eurobarometer, 2011a: 2011b). Secondly, people are disconnected to environmental consequences, which are often evaluated as uncertain, as those risks are perceived as being spatially and temporarily remote risks, affecting future generations and other countries, (Maibach et al., 2009; Upham et al., 2009; APA, 2009). Gilford et al. (2008) described this issue as, “Temporal pessimism” and, “Spatial optimism”. “Temporal pessimism”, means that environmental quality will decrease over time, whereas, “Spatial optimism”, implies that environmental quality worsens as geographic distance increases. Research to date suggests that there is one exception to this ranking of individual concerns; energy security. For example, DECC (2012), found that in general, concern about energy security to be higher than concern about climate change and that 40 percent of those surveyed were concerned with steep rises in energy prices.
  • 55. 3. Energy use behaviours: motivations and barriers 35 Thirdly, understanding environmental issues is a complex topic and there is noticeable doubt about the validity of scientific findings, such as climate change and the degree of anthropomorphic contribution to it, (BBC News, 2010; IPPR, 2009; Leiserowitz et al., 2011a; Reynolds, Bostrom, Read, & Morgan, 2010). This complexity, in conjunction with individual detachment, to the topic can lead to a perceived disempowerment and belief that individuals cannot do anything, or, are not responsible for solving the problem, (Brouwer et al., 2008; Martiskainen, 2007; S.C. Moser & Dilling, 2004; Whitmarsh, 2009). Fourthly, engaging in some type of pro-environmental behaviours can provide a feeling of having done their bit, regardless of the limited impact their actions might actually have, which then can result in ascribing further responsibility to others to take additional actions, (Prendergrast et al., 2008). Weber (1997) described this as the “Single action bias”, representing the tendency individuals have to engage in single corrective actions, making them less likely to take additional steps if the first action is not the most effective one and presumably, because the first action succeeded in reducing their feeling of ”Worry or vulnerability”. In addition to this, feeling responsible for solving the problem can be influenced by time and space where individuals pay more attention to near-term threats and care for their family and friends, (Slovic, 2000; Slovic, Finucane, Peters, & MacGregor, 2004; Weber, 2006). Such responsibility to care for becomes looser once discussing future generations or more abstract locations, such as the nation, or the world. Following the time/space phenomenon and the resulting individual detachment, immediate threats such as a shortage in energy supply are more relevant and of greater urgency than future problems, for example climate change, (Slovic, 2000; Slovic et al., 2004; Weber, 2006). Lastly, this understanding of shared responsibility in solving the problem implies a need for a collective effort, (Leal Filho, 2011) and where free-riders can cause a lack of collective motivation to act more pro- environmentally. Free-riders are usually individuals who are extremely resistant to changing their own actions and instead enjoy the benefit accrued from collective effort, but contribute little or nothing to the effort of achieving the common goal, (IPPR, 2009; Maibach et al., 2009; Upham et al., 2009). Common free- riders within an environmental context include, all others, other countries and the enterprise sector, with examples for the latter being shopping centres that leave their lights on all night, or distant activities, such as engaging in deforestation outside of national boundaries. As Garvey (2009) summarized, “The sea level
  • 56. 3. Energy use behaviours: motivations and barriers 36 will be where it will be in 2050 whether this wine bottle is recycled or not. So why bother?”. Such a conscious denial of personal responsibility is also known as the “Passive bystander” effect, (Marshall & Lynas, 2003), or “Bystander effect”, (Darley & Latane, 1968) and can reflect low individual efficacy on contributing towards solving the problem, (Lorenzoni & Pidgeon, 2006; Upham et al., 2009). The passive bystander effect expresses the way in which individual responses are influenced by the responses of those around them. Previous experience demonstrated the individuals’ tendency to social conformity and the social influence from family, friends or neighbours, which might be illustrated as “If others don’t do it, it’s rather not important, so why should I care”, (Thaler & Sunstein, 2008). This is to say that individuals hold low expectations about the impact of their own actions, but at the same time, they strongly believe that if a large number of individuals would engage in those same actions then that would have an impact and could solve the problem, (Maibach et al., 2009). But by doing this it also increases the feeling that individuals’ actions do not make a difference on their own. The, free-rider, problem is therefore one where, what as a group could be called a rational response, meaning to take action, becomes irrational for an individual, if no other bystander seems to have any intention to act; the idea of “I will if you will”. The, free-rider, problem connects to the, “Tragedy of the commons”, dilemma, (Hardin, 1968; Jager, Janssen, Vries, Greef, & Vlek, 2000) in which the behaviour that is in the individual’s interest is not optimal from the group’s aggregate perspective and vice versa. This is where multiple individuals, acting independently and rationally in their own self-interest, ultimately deplete a shared, limited, resource, even once it is clear that it is not in anyone's long-term interest. This can lead to a feeling of powerlessness, since if people perceive they cannot change a situation they will very likely retreat into apathy and resignation and thus will be less likely to address environmental issues, (Kollmuss & Agyeman, 2002; S. C. Moser, 2007; S. C. Moser & Dilling, 2004). As such there appears to be a wealth of literature findings that explains why positive attitudes, concerns and awareness regarding the environment might not result in pro-environmental and energy efficient behaviours at home.
  • 57. 3. Energy use behaviours: motivations and barriers 37 3.3 Barriers to adopting more energy efficient behaviours In accordance with the literature there appears to be a number of barriers that could influence the adoption of more energy efficient behaviours. Even where individuals are concerned about the environment, or are motivated to save money by reducing their energy use, the adoption of more energy efficient behaviours can often have negative connotations associated with giving up something, a discomfort, a restricted lifestyle, or a more general reduction in their quality of life, (Barenergy, 2011; Kaplan, 2000). 3.3.1 Monetary focus as a barrier A focus on saving money as a motivation to save energy might ultimately form a barrier, for the following reasons. Firstly, a focus on saving money can contribute to feelings of boringness and hassle, caused by the effort required to engage in numerous actions, that at the end of the day result in only minor monetary savings, (Green Alliance, 2011; IPPR, 2009). Secondly, a focus on saving money could lead to the rebound, or take back effect (see section 2.2.8.). Thirdly, for most households, except those in fuel poverty, energy bills account for a small (3-4 percent) share of disposable income, which might result in a lack of motivation for people to take meaningful actions to save energy at home, (BPIE, 2011). As such, money as a motivation to less energy use appears to be a barrier towards actually realizing energy savings. 3.3.2 External/macro barriers: policy based, structural and economic barriers The literature posits that there are a number of external/macro barriers, namely policy based, structural and economic barriers that can influence energy use at home. Politicians develop frameworks, such as laws, directives or regulations, which can facilitate, or work as a barrier to, the adoption of more energy efficient behaviours, (Barenergy, 2011). Policy making can organise opportunities to foster innovation and technology take-up, but also to set the ground for promoting pro-environmental behaviours, or to prohibit those behaviours that are not in the interest of the individuals or the society, (Green Alliance, 2011). The introduction of congestion charges and the defining of standards for buildings and electrical appliances, are examples for how policy based interventions can influence the adoption of more energy efficient behaviours. Policy based interventions can however also create a barrier. If charges and standards are set
  • 58. 3. Energy use behaviours: motivations and barriers 38 too low, they might not have much influence with regards to behavioural change, but rather work as an indicator of what is socially expected. An example for this would be the current policy attempts to assure that energy supply would always match growing demand; where energy intensive behaviours are not challenged, but rather accepted and supplied, (Green Alliance, 2011). Further to this, physical-structural barriers, such as the available infrastructure of the buildings, or the availability and economic viability of technological solutions, also influence the degree of freedom and opportunity to adopt more energy efficient behaviours, (Barenergy, 2011). Such physical-structural barriers can lead to so called locked-in situations, such as being locked into poorly built and inefficient housing, (Goldblatt, 2005; Maréchal, 2010; Martiskainen, 2007). Overcoming physical-structural barriers thus requires refurbishment of older housing and making available new physical-structural infrastructures, such as the introduction of more energy efficient products. Removing physical-structural barriers does however not necessarily lead to realizing energy savings due to, for example, rebound and take back effects, or due to the energy efficiency gap, (Maibach et al., 2009). In addition to this there might also be economic barriers, such as required initial investment, or the capability and willingness to invest, (Barenergy, 2011), that can play a crucial role in this and act as a disincentive to adopt more energy efficient behaviours, (IPPR, 2009). With regard to these, there also appears to be a preference of short-term gains compared to long-term ones, (Nordlund & Garvill, 2002, 2003; Stern, 2000; Thøgersen & Ølander, 2002), as well as a preference for action when these create potential gains, rather than taking action to avoid potential losses, (Tversky & Kahneman, 1991). For example, one might prefer to refurbish the kitchen that results in immediate benefits, rather than to exchange the boiler for a more energy efficient one so as to save money in the medium-long term. More environmentally friendly options are often also more expensive than standard appliances or services, (Barenergy, 2011) and thus constitute an additional barrier, (Leiserowitz et al., 2009). Economic barriers thus perhaps influence efficiency behaviours more strongly than curtailment ones, since curtailment behaviours often do not require an investment. In addition to this, home appliances may have long lifetime spans and are purchased infrequently. As a result substituting them might not always be beneficial in environmental terms and would require complex calculations outside the ability of most ordinary people, (DGGE/IP-3E, 2004; Leiserowitz et al., 2009; Quercus, 2008). Addressing economic barriers has thus proved
  • 59. 3. Energy use behaviours: motivations and barriers 39 to be a challenging topic that might require governmental interventions, such as homeowner tax breaks and subsidy programmes, to support and accelerate the diffusion of more energy efficient appliances and solutions, (Leiserowitz et al., 2009). 3.3.3 Knowledge based barriers Lack of individual knowledge can also constitute a barrier for the adoption of more energy efficient behaviour since they might not know how to behave more efficiently, or do not have the time to research which options are best, (Leiserowitz et al., 2009). Knowledge based barriers are associated with a lack of access, or difficulty in understanding relevant information, such as regarding different options and the potential benefits of those different options, (Barenergy, 2011; Leiserowitz et al., 2009). Information might entail accessing different sources, from a more structural level, such as fiscal, legal, regulatory, to a more individual level of cost, awareness, or benefits. Previous research indicates however, that there appears to be a good level of knowledge regarding topics such as the contributions of behaviour to causes, impacts and solutions of climate change, (Brouwer et al., 2008; Eurobarometer, 2011b; Whitmarsh, 2009). These findings equally show that levels of knowledge and engagement decrease once the context moves from climate change to more specific issues, such as carbon reduction, or energy use, (Baird & Brier, 1981; DEFRA, 2007; Gatersleben, 2000; Upham et al., 2009; Whitmarsh et al., 2009). These decreasing levels of knowledge might thus be a barrier for what the individual understands to be links between behaviour and lifestyle at home and increase in energy use, carbon consumption and CO 2 emissions, (Brandon & Lewis, 1999; Darby, 2006; Upham et al., 2009; Future Foundation, 2006). In addition to this previous research suggests that there is low salience of climate change, energy and environment in individuals’ day-to-day choices and actions, (Brook Lyndhurst, 2007; Giorgi, Fell, Austin, & Wilkins, 2009). This highlights a potential dissonance between the growing knowledge and awareness of environmental problems at a general level, that does not translate into personally relevant behaviours and thus constitutes an information-behaviour gap, (Energy Saving Trust, 2011; Martiskainen, 2007). Previous studies in Portugal equally reveal a lack of information regarding the most relevant energy uses at home in terms of their relative proportion to the monthly energy bill, which indicates a dissonance between the actual and the perceived energy use of different categories of home appliances, (Quercus, 2008).
  • 60. 3. Energy use behaviours: motivations and barriers 40 3.3.4 Cultural – normative and social barriers Cultural prerequisites and social norms that set aesthetics, comfort or even social position, can also work as barriers towards adopting more energy efficient lifestyles, (Barenergy, 2011). To resolve such barriers requires a clear understanding about the social processes within which decisions are made, (Carpenter, Folke, Scheffer, & Westley, 2009; Folke, 2006). Energy saving behaviour challenges existing ways of thinking and doing, including social customs and the ways of living, as well as the assumptions that support these attitudes and behaviours, (Sedgwick and Edgar, 1999). Within current lifestyles, most of the energy related services are perceived as necessary for meeting basic needs and social practices. Therefore, energy consumption has been driven by evolving expectations and standards of what is normal, (Heiskanen, Johnson, & Vadovics, 2009; Quitzau & Røpke, 2008; Shove, 2003). Examples of such evolving practices and norms are plenty, including the aesthetics question of solar panels, (IPPR, 2009), to energy efficient lighting, (Leiserowitz et al., 2009), the social taste for ambient low-lighting, (Barenergy, 2011; Southerton et al., 2011; Wilhite & Lutzenhiser, 1999), or the importance of evolving cooling (and heating), practices at home, (Shove, 2005; Wilhite and Ling, 1992). These cultural, normative and social settings help to frame normal behaviour and expectations concerning the consumption of energy and therefore, work as a barrier to the adoption of energy-saving behaviours, (Southerton et al., 2011). Therefore, energy consumption might not only be, individually invisible, but also, socially invisible and rarely the subject of conscious decision, (Lutzenhiser, 1993). Changing these social customs and norms is both difficult and problematic, as it requires shifting the focus of intervention away from individual consumer decisions, toward shaping and intervening in the shared behaviours of social groups, (Southerton et al., 2011). 3.4 Individual psychological barriers Individual psychological barriers are the product of the existing cultural, normative and social expectations that support the individual perception regarding limits to what people are willing to do to save energy, with these limits often being rooted in personal experiences, or upbringing, (Barenergy, 2011). In this context psychological barriers can help to explain an existing unwillingness to adopt more energy efficient behaviour and thus constitute barriers and as further examined in the following.
  • 61. 3. Energy use behaviours: motivations and barriers 41 3.4.1 Habits as a barrier Energy use at home is often the outcome of established habits and practices that can constitute a barrier towards the adoption of different and more energy efficient behaviours, (Darnton, 2008; Jackson, 2005; Martiskainen, 2007; Prendergrast et al., 2008; Upham et al., 2009). Habits thus can act as a determinant of domestic energy use and are seen to be one of the reasons why energy consumption keeps rising despite an evident increase in awareness and concern about energy use at home, (Maréchal, 2010). Indeed, energy consuming behaviours, such as switching off the lights, or turning off appliances, are often guided by deeply ingrained habits and therefore can become counter-intentional to individual best intents, (Verplanken & Faes, 1999). Counter-intentional habits represent a kind of cognitive trap, that locks individuals into routine behaviours, even when these behaviours conflict with the individual’s rational deliberations, or that are inconsistent with social norms, (Jackson, 2005). Counter-intentional habits might thus help explain the, efficiency paradox and continued increase of energy consumption despite rising environmental awareness among the population, (Maréchal, 2010). Such deeply ingrained habits could lead to locked-in practices, where individuals become locked-in into their daily energy consumption behaviours, (Maréchal, 2010). This makes them less open to rational deliberation and thus cryptic to understand, which limits the individual’s response to policies, as well as behavioural change interventions, designed to promote the adoption of more energy efficient behaviour, (Jackson, 2005; Stern, 2007). As a result, habits can become behaviours that are difficult, (Bamberg, 2003), although not impossible to change, (Matthies, Klöckner, & Preißner, 2006). 3.4.2 Comfort as a psychological barrier The expectation of individual comfort is considered to be an important psychological barrier to any attempt to reduce energy consumption, (Huebner, Cooper, & Jones, 2011; Shove, 2003). The distant and sometimes invisible, negative consequences of environmentally damaging, or energy intensive behaviours, seem to be overpowered by the relatively immediate certainties of a reduction in comfort and convenience, (Lehman & Geller, 2004). Understanding the detail to what constitutes comfort requires one to consider contextual, social, technological, cultural, historical and psychological factors, (Hitchings, 2009; Shove, 2003, 2006). Recent trends suggest a large variation in comfort conditions and practices, (de Dear & Brager, 2001;
  • 62. 3. Energy use behaviours: motivations and barriers 42 Hitchings, 2009), but also a decreased level of individual thermal adaptability due to the growing attraction of setting unsustainable ambient standards, (de Dear & Brager, 2001). In global terms, the energy cost of maintaining standardized comfort conditions in buildings and in indoor environments around the world is ultimately unsustainable, (Shove, Heather, Lutzenhiser & Hacket, 2008). Although people have reported being comfortable in a temperature range of 6 – 30 o C, (Chappells and Shove, 2005), comfort expectations are converging towards artificially heated and cooled environments, which increase energy and resource use, particularly as air-conditioning gains prominence in households, (Cooper, 1998; Ackermann, 2002). Today most people tolerate a narrower temperature band and reject former ways of achieving comfort, such as opening windows, using blankets and appropriate clothing, building thermally efficient housing, or taking siestas on hot afternoons, (Shove, 2003). Therefore expectations about what type of thermal comfort is desirable (humidity levels, temperature, etc.), as well as how that comfort should be achieved, are converging towards air-conditioned environments, (Strengers, 2008). Despite the direct link between comfort, peak demand and demand management, current expectations of comfort are still considered to be a basic, non-negotiable human right in developed nations, rather than being understood as unsustainable, (Strengers, 2008). 3.4.3 Individual beliefs and self-efficacy as a barrier An individual’s belief about the ease or difficulty of performing a given behaviour, or on being capable of achieving a particular goal, is seen to influence individual decision on whether or not to conduct a behaviour, (Martiskainen, 2007). From literature this belief has been observed in studies on self-efficacy expectancies, (Bandura, 1986), perceived behavioural control, (Ajzen & Madden, 1986), locus of control, (Maddux, 1995), ability concepts, (Ølander & Thøgersen, 1995), or sense of agency, studies, (Jeannerod, 2003). Such studies all show that one’s behaviour can have an impact and that one is capable of controlling the outcomes of one’s own behaviour. This involves both beliefs about the likelihood between certain behaviours and desired goals or outcomes (outcome expectancies) and beliefs about an individual’s ability to execute the behaviours (self-efficacy expectancies). In his original work Bandura (Figure 3-1) referred to such a distinction as “Efficacy expectations” and “Outcome expectations” with the former meaning “The
  • 63. 3. Energy use behaviours: motivations and barriers 43 conviction that one can successfully execute the behaviour required to produce outcomes” and the latter as “A person’s estimate that a given behaviour will lead to certain outcomes”, (Bandura, 1977a, p. 193). Figure 3-1: Diagrammatic representation of the conditional relations between efficacy beliefs and outcome expectancies (adapted from Bandura (1977b), p. 350). Bandura justifies this distinction on the ground that “Individuals can believe that a particular course of action will produce certain outcomes, but if they entertain serious doubts about whether they can perform the necessary activities such information does not influence their behaviour”, (Bandura, 1977a, p. 350). Efficacy beliefs are thus seen to influence the initiation and persistence of behaviours and courses of action, thus they are assumed to be specific to behaviours and situations, (Bandura, 1977a, 1982, 1986). As a consequence, perceived efficacy in one behavioural-situational domain could therefore be expected in other domains depending on the extent to which the behaviours and situations share crucial features and require similar skills and functions, (Bandura, 1990). For instance, perceived efficacy in recycling might, or might not, be expected to occur with energy saving at home, depending on how the two behaviours are evaluated. Individual beliefs, regarding self-efficacy, can be learned in various ways, including personal or vicarious experiences, learning influenced by individual attempts in a given task, the degree of persistence in doing so and ultimately success of the action, (Bandura, 1977a). Bandura (1977a), hypothesized that self-efficacy affects choice of activities, effort and persistence with success, or failure, in personal performance being proposed as the most powerful influence on self-efficacy. Successful personal experiences raise self-efficacy and failures lower it, but once a strong sense of self-efficacy is developed, a failure may not have much impact, (Bandura, 1986). For example, if someone is attempting to save energy and registers a decrease on the energy bill, this could contribute to the perception of self-efficacy via successful energy saving. The opposite, an increase on the energy bill, might contribute to belief failure and lack of efficacy in saving energy. This building of personal experience is seen to be particular important, since people tend to hold onto beliefs and do not abandon them, even after receiving contradictory information, (Anderson, 2007). Person Behaviour Outcome EFFICACY BELIEFS Level Strength Generality OUTCOME EXPECTANCIES Physical Social Self-evaluative
  • 64. 3. Energy use behaviours: motivations and barriers 44 Individuals can hold many beliefs about any given behaviour, but they can attend to only a relatively small number of beliefs at any given moment and it is this small number of salient beliefs that are considered to be the prevailing determinants of a person’s intentions 10 and behaviours, (Ajzen, 1991). In the case of energy this could be, for instance, to decide between adding another layer of clothes or maintaining a higher room temperature for perceived comfort needs. This is to say that, if one’s previous experience reinforces self-efficacy in saving energy at home, one might persist in the effort. In the case of failure this might lead to the abandonment of further attempts to save energy at home. Once individual self-efficacy and competence are extended to a group level, a collective efficacy can be observed. Individual responses are not entirely independent of responses from others, from what is perceived as the social norm and therefore a sense of collective efficacy does exist where individuals can solve their problems and improve their lives through concerted effort, (Bandura, 1986). Research by Andreasen (1995) further revealed that there might be a perceived lack of collective capacity that together with a perceived opposition and a perceived social mandate, can constitute the key reasons for individual inaction. This perceived lack of capacity might thus occur once the target audience no longer believes that they can carry out an action and maintain it, (Bandura, 1977a, 1992; Rotter, 1954; Schwartz, 1977; Stern, 1999). For instance, believing one has no control over climate change could facilitate mechanisms such as denial and work against pro-environmental behaviours, (Gifford, Iglesias, & Casler, 2008). Baker and Kirsch (1991) found that once people anticipated aversive outcomes, they were no longer willing to engage in a behaviour that may produce those outcomes. Their linguistic habit is to say that they cannot perform the behaviour (low self-efficacy), rather than saying that they will not perform it. This then might overestimate the prevalence of lack of efficacy and also generate apathy and an increased sense of helplessness towards environmental issues, (Allen & Ferrand, 1999; Donn, 1999; Vandenbergh, Barkenbus, & Gilligan, 2008). 3.4.4 Resistance and unwillingness to change as a barrier Resistance and unwillingness to change often results from deeply ingrained habits, existing and commonly accepted standards, or social norms, such as maintaining the current levels of comfort and wellbeing, that 10 An intention is what one says one plans to do.
  • 65. 3. Energy use behaviours: motivations and barriers 45 all can be considered as a barrier towards the adoption of more energy efficient behaviours, (Barenergy, 2011; Darnton, 2008; Darnton, Verplanken, White, & Whitmarsh, 2011; EEA, 2013; Gardner & Stern, 2008; Jackson, 2005; Prendergrast, Foley, Menne, & Isaac, 2008; Shove, 2003). Research has provided some evidence for a number of behaviours in terms of how willing people are to engage in them in order to protect the environment. They found that individuals are generally receptive towards recycling and the conservation of energy at home, but noted considerably resistance to changing personal habits, such as travelling, (DEFRA, 2007; Thomas & Sharp, 2013; Tobler et al., 2012; Upham et al., 2009; Whitmarsh, 2009; Whitmarsh, Turnpenny, & Nykvist, 2009; Williamson, Soebarto & Radford, 2010). Travel habits seem to be the hardest to change; personal resistance and unwillingness to change are a prime barrier for this, (Tobler et al., 2012). 3.5 Concluding remarks This chapter looked at what influences energy use at home (RQ2), and the underlying motivational variables and barriers for adopting more energy efficient behaviours. As can be seen, maintaining existing energy related behaviours appears to outweigh the motivation to adopt more energy efficient ones as a result of a number of macro, knowledge related, cultural, normative, social and psychological reasons, that constitute barriers towards change. Even motivations, such as realising monetary savings, ultimately can constitute a barrier. Potential benefits seem to directly compete with the effort that would be required to engage in the numerous actions required to actually achieve meaningful savings, (BPIE, 2011; Green Alliance, 2011; IPPR, 2009; Leiserowitz et al., 2009), as well as competing with a perceived loss in terms of desired level of comfort and wellbeing, (Barenergy, 2011; Darnton, 2008; Darnton, Verplanken, White, & Whitmarsh, 2011; EEA, 2013; Jackson, 2005; Shove, 2003). Other motivations, such as the need to comply with social norms, or to comply with personal, altruistic and moral motivations, do not appear to constitute an important motivation to adopting more energy efficient behaviours at home, (IPPR, 2009; Leiserowitz et al., 2009). From a barrier perspective, all such factors could however prevent the adoption of more energy efficient behaviours (RQ2b). This seemed to be, in particular, true for family related comfort levels where there is considerable resistance to change ingrained behaviours particularly those that are perceived as normal and socially acceptable, (DEFRA, 2007; Tobler et al., 2012; Upham et al., 2009; Whitmarsh, 2009; Whitmarsh et
  • 66. 3. Energy use behaviours: motivations and barriers 46 al., 2009). A barrier towards change frequently results from a resistance to making changes that are perceived as reducing quality of life, (Kaplan, 2000), while preference is given to easy to do habits, such as switching the lights off, or recycling, (Thøgersen & Ølander, 2002). As can be seen through this chapter, barriers for adopting more energy efficient behaviours at home (RQ2b), might also include (1), The lock in effect of infrastructures and existing social conventions, such as comfort and convenience, (Heiskanen et al., 2009; Jackson, 2005; Martiskainen, 2007).(2); The attitude/value-behaviour gap, (Kollmuss & Agyeman, 2002). (3); The disconnection towards environmental risks, concerns and problems which are overall perceived as spatially and temporarily uncertain, (Eurobarometer, 2011a; 2011b; Leiserowitz et al. 2011a; 2011b, Maibach et al., 2009; Upham et al., 2009); (4), Required engagement in numerous small actions, (Kates et al., 2001; Weber, 1997); (5), The invisibility of the consequences of ones actions, (Thøgersen, 2005); (6), Social dilemmas, since individual efforts are understood as useless unless others participate or contribute as well, (Kollock, 1998; Maibach et al., 2009; Thaler & Sunstein, 2008; Uusitalo, 1990); free-riding as a problem in itself and as a justification for resistance to change ones own actions, (IPPR, 2009; Maibach et al., 2009; Upham et al., 2009); (7) Political and economic barriers that could promote and facilitate the adoption of more energy efficient behaviours, (Green Alliance, 2011); (8), Cultural-normative barriers as social practices influence energy consumption driven by evolving expectations and standards of normal everyday life, (Heiskanen et al., 2009; Quitzau & Røpke, 2008; Shove, 2003; Southerton et al., 2011); or (9) Knowledge based barriers as individuals may not always be aware of the environmental impacts of behaviours, or benefits of changes in these behaviours, (Baird & Brier, 1981; Gatersleben, 2000), including lack of access to relevant information, (Barenergy, 2011; DEFRA, 2007; Energy Saving Trust, 2011; Leiserowitz et al., 2009; Martiskainen, 2007; Upham et al., 2009; Whitmarsh et al., 2009). In terms of psychological barriers (RQ2c), it can be seen that adopting more energy efficient behaviour might require increasing efficacy expectations and outcome expectations, (Bandura, 1977a; Martiskainen, 2007). Anticipating aversive outcomes, be it low or undesired impacts, might explain why people report not being capable to perform a behaviour (low self-efficacy), rather than saying that they will not perform it, (Baker & Kirsch, 1991). This then might generate apathy and an increased sense of helplessness, (Donn, 1999), or a reduced participation in environmentally significant behaviours, (Allen & Ferrand, 1999). Thus it
  • 67. 3. Energy use behaviours: motivations and barriers 47 can be seen that to successfully address environmental problems will require a collective effort and efficacy, which then brings along the psychological barrier of “I will if you will”, (Vandenbergh et al., 2008). Further It can be seen that the aspects of time and space, and short-term (economic), focus can lead to a lack of consideration for longer-term impacts / interconnections of actions and decisions, (Nordlund & Garvill, 2002, 2003; Stern, 2000; Thøgersen & Ølander, 2002). Currently there appears to be no clear data for Portugal on whether such aspects of time and space, short-term focus and longer-term impact can be observed. The literature provides little evidence regarding the ability of values and attitudes to influence the amount of energy being used at home. For the case of values, literature indicates that values have a loose influence on behaviour, (Rohan, 2000), affecting behaviour indirectly through specific beliefs, norms and intentions, (Feather, 1990; Nordlund & Garvill, 2003; Poortinga et al., 2004), though value-action gaps could also be observed, (Verplanken & Holland, 2002). Similarly, the contribution of attitudes as a predictor of pro- environmental behaviours seems not to be well established, despite the existence of available studies, (Bamberg, 2003; Geller, 1981; McKenzie-Mohr & Smith, 1999; Poortinga et al., 2004; Schultz et al., 1995; Thøgersen, 2004). As seen from the literature there might also be an attitude-behaviour gap, (Kollmuss & Agyeman, 2002). Though attitudes seem to guide behaviour for those cases where attitudes are strong and where social and structural conditions support the behaviour, (Stern, 2000), or for changing simple, repetitive, low-cost energy saving behaviours, (Abrahamse & Steg, 2009; Abrahamse et al., 2005; Black et al., 1985; Heberlein & Warriner, 1983; Stern, 1992), as well as for having the financial ability to perform the behaviour, (Gatersleben, 2000). This might be, in particular, problematic, since energy consuming behaviours are often habitual and therefore difficult to modify, (Bamberg, Ajzen, & Schmidt, 2003), although not impossible to change, (Matthies et al., 2006). It thus appears that to encourage the adoption of more energy efficient behaviour would likely require overcoming a number of barriers, including individual psychological ones. Altogether this would therefore imply a need for better understanding of, for example, the social processes within which decisions are made, (Barenergy, 2011; Carpenter et al., 2009; Folke, 2006), or how the cultural, normative and social settings impact to frame normal behaviour, (Maréchal, 2010).
  • 68. 4. Energy use and intervention strategies 48 4 Energy use and intervention strategies This chapter looks at the potential effectiveness of change interventions within the field of energy use at home (RQ3) and the different types of interventions that might be applied. Achieving lasting behavioural change appears to be often problematic and environmental values, beliefs and attitudes do not appear to have a significant influence on energy consumption, (Martiskainen, 2007; Upham et al., 2009). Some agreement exists that, promoting behavioural change requires a combination of effort, from communication to policy making, to reduce the various barriers that exist (IPPR, 2009). To date, most intervention strategies have, however, predominantly focused on voluntary behavioural change, rather than on changing contextual factors that can determine individual decisions, (Abrahamse et al., 2005; Jackson, 2005). Contextual factors set the context where individual decisions are made and intervention strategies, that do include both voluntary behaviour change and contextual factors, might therefore increase the level of success in promoting lasting behavioural change, (Gärling et al., 2002). Common contextual factors include technological developments, economic growth, demographic factors, institutional factors and cultural developments, (Gatersleben & Vlek, 1998), that together, shape individual factors, such as motivations, opportunities and abilities, (Ølander and Thøgersen, 1995). Findings from Abrahamse et al. (2005), suggest that once voluntary behaviour change and contextual factors are applied together, then behavioural change interventions might also be able to target the individual’s perceptions, preferences and abilities. They might equally change the context in which decisions are being made (for instance, through financial rewards, laws, or the provision of energy-efficient equipment) and as a result they could make energy saving behaviour relatively more attractive. For instance, households may save more energy by properly insulating their homes than by lowering thermostat settings. However, the use of energy-efficient appliances does not necessarily result in reduction of the overall energy consumption, which in part is a consequence of a rebound effect, (Berkhout, Muskens, & Velthuijsen, 2000). To avoid a rebound effect might require intervention strategies that provide the right interplay between contextual factors and micro-level factors, though the literature on combined intervention strategies appears to be scarce and there is apparently little evidence about the actual impact of such combined intervention
  • 69. 4. Energy use and intervention strategies 49 strategies, (Abrahamse et al.; 2005). In addition to this, it is often difficult to establish the contribution of each of the interventions separately and the volume and consistency of the evaluations that are currently available has been very poor, often vague and generic with very little empirical rigour presented, (Southerton et al., 2011). 4.1 Energy use, Interventions and supportive frameworks There are a number of frameworks within the environmental field that attempt to support intervention strategies to find the right interplay between the various existing factors. Frameworks from the field of behavioural economics approach the matter, for example, by putting forward a set of external, internal and social determinants, so as to understand individual behaviour. The overall aim, as illustrated in Figure 4-1, is to provide an integrated approach to change behaviour through a number of external, internal or social factors, such as emotions or habits, which could change the balance of costs vs. benefits that is at the centre of the traditional economic perspective of understanding human behaviour, (Prendergrast et al., 2008).
  • 71. 4. Energy use and intervention strategies 51 From a behavioural economic perspective, it is argued that individual behaviours are influenced by a much wider range of factors and not limited to one’s, ‘expected net benefits’. Such factors include, for example, the impact of habits, emotions, cognitive capabilities, cultural attitudes and social norms. From an economic perspective all of such factors can thus impact the balance of an individual’s costs vs. benefit understanding and thus impact behaviour, (Prendergrast et al., 2008). As such, informational and financial levers alone might not be sufficient to explain an individual’s behaviour and that the prevailing rational model of behaviour is, in some circumstances, inappropriate once one considers how people make decisions, (Prendergrast et al., 2008). Another framework within the environmental field that attempts to support intervention strategies to find the right interplay uses psychological interventions as a framework and tool to promote individual behavioural change. Focus is laid on changing existing perceptions, knowledge, attitudes, norms and values under the assumption that this then would result in behaviour changing accordingly, (Abrahamse et al., 2005). Intervention can then address the community level and the social aspects of energy-related behaviour, instead of the individual approach that has been dominating the area, (Abrahamse et al., 2005; Darby, 2006; Heiskanen et al., 2009; Middlemiss, 2008). Another framework that could potentially be used to support intervention strategies is a model developed by DEFRA (UK Department for Environment, Food and Rural Affairs), under the UK’s strategy to promote pro-environmental behaviours, as depicted in Figure 4-2 and which works alongside the four E factors, Enable, Engage, Exemplify and Encourage, (DEFRA, 2008).
  • 72. 4. Energy use and intervention strategies 52 Figure 4-2: Diagrammatic representation of the 4E’s model, (DEFRA, 2008, p. 53). As can be seen from Figure 4-2, promoting pro-environmental behaviour from the DEFRA 4E Model framework perspective would require a number of actions to result in habits being broken and new more environmental friendly behaviours adopted. A further framework to support intervention strategies is the Mindspace approach, (Dolan, 2010), which intends to take behavioural science to the very heart of policy-making. The word, Mindspace, is itself a mnemonic of nine non-coercive influences on behaviour, as Figure 4-3 shows: Figure 4-3: Mindspace’s influences on behaviour, (Dolan, 2010). From a Mindspace framework perspective, the approach seeks to influence behaviour by changing the context, which would encourage people unconsciously into one course of action, rather than another.
  • 73. 4. Energy use and intervention strategies 53 In summary, it can be clearly shown that there are a number of frameworks that attempt to support intervention strategies to find the right interplay between the various existing factors that could be used to encourage the adoption of more energy efficient behaviours. Each framework shows a slight variation in terms of existing factors and approach. 4.1.1 Potential intervention layers As much as the right interplay between the contextual factors and micro-level factors influence energy use at home, so do a diversity of determinants, motivations and barriers. They all are considered influential to energy use at home and thus might be taken into account for any intervention attempts. Behavioural change interventions tend to address at least one of the contexts in which behaviour might be changed, individual, social, or contextual/material spheres, (Southerton et al., 2011), as illustrated in Figure 4-4. Figure 4-4: The relation between material, social and individual contexts, adapted from Southerton et al. (2011). Figure 4-4 illustrates that influencing the individual sphere might require interventions to focus on the individual attitudes so as to change behaviours and choices. Within the social sphere, such interventions will address social norms, cultural conventions and shared understanding of practices. In the contextual/material sphere, intervention might refer to the objects, technologies, and infrastructures, which can enable or constrain the adoption of new behaviours, (Southerton et al., 2011). Following from this, Figure 4-5, builds from Barenergy (2011) and summarizes what could motivate, enable and reinforce
  • 74. 4. Energy use and intervention strategies 54 individual behavioural change in relation to the barriers, that literature indicates exist, that need to be addressed and finally, the type of interventions that could be used in order to promote change. Figure 4-5: The relation between energy use determinants, motivations, barriers to change and types of intervention, adapted from, (Barenergy, 2011). As Figure 4-5 illustrates, there might be two different layers of intervention. One that addresses the external/macro factors, such as the need of an adequate legal framework, or the deployment of financial instruments, that could promote individual change and one that promotes internal change by influencing values, beliefs or perceptions. Comfort, convenience, individual willingness, motivation, opportunity and ability are all identified determinants that influence energy use at home and as have been detailed through Chapters two and three. Thus there appear to be a number of intervention layers (Fig 4-4) and factors (Fig 4-5), though the literature appears undecided as to which could encourage lasting change. 4.2 Behavioural change, communication and persuasion Persuasion can influence others by modifying their beliefs, values, or attitudes, (Simons, 1976, p. 21) and ultimately their behaviour, (Jackson, 2005; Martiskainen, 2007). Persuasion is often based on three principles; (1), the credibility of the sender (2), the persuasiveness of the argument/message and (3), the
  • 75. 4. Energy use and intervention strategies 55 responsiveness of the audience, (O’Keefe, 1990). Persuading people to change can be particularly difficult in a message-dense environment and effective persuasion requires a number of principles to be met such as, understanding the target audience, using emotional and imaginative appeals, immediacy and directness, commitments/loyalty schemes and the use of ‘retrieval cues’ to catalyse the new behaviour, (Jackson, 2005). There are a number of persuasion theories and approaches that might be applied to promote behavioural change. The cognitive dissonance theory, (Festinger, 1957) assumes, for example, that people prefer congruency, i.e. people are motivated to avoid internal inconsistency (dissonance), between values, beliefs, attitudes and behaviour. These feelings of discomfort might arise from conflicting attitudes or values, but might equally be invoked by discrepancies between an attitude, e.g. about the self, and behaviour highlighting the desire for attitude-behaviour consistency, (Jackson, 2005). The theory suggests that once engaging in a behaviour that opposes attitudes, people experience distress and an uncomfortable psychological state resulting from the awareness of holding conflicting beliefs, or acting inconsistently with one’s attitudes. Depending on the importance of the issue and the degree of discomfort, people then will be persuaded to change beliefs, attitudes or behaviours in order to reduce inconsistencies in the cognitive information that they hold about themselves, their behaviour, or their environment, (Brehm & Kassin, 1996; Dainton & Zelley, 2005). In accordance to Brehm and Kassin (1996), people tend to adopt one of three strategies to reduce dissonance: (1), changing their attitude to justify their behaviour, particularly for long-term habits where it is suggested that people readjust their long-term goals rather than, “changing the habit of a lifetime”, (Jackson, 2005, pp. 114-115). An example of this would be the London congestion charge, where public opinion was opposed before it was introduced, but seems to have changed once the charge was introduced, (Darnton, 2008; Knott et al., 2008). (2), Claiming, or perceiving, to have little or no choice of action, i.e. reducing dissonance by under-reporting knowledge about the impact of particular behaviours, (Darnton, 2008), For example, under-report knowledge on how to reduce energy use in order to reduce the unavoidable contradiction in responses to questions about personal energy use. This could be one of the reasons for decreasing levels of reported knowledge once moving from bigger issues, such as climate change, towards more specific behaviours, such as energy saving at home. (3) By denying any inconsistency, i.e. denying personal responsibility for tackling the problem, or by ‘over-claiming’ the involvement in,
  • 76. 4. Energy use and intervention strategies 56 “Issues which people think they ought to be seen to be involved in”, (Darnton, 2008, p. 12). With regards to denial of inconsistencies, the literature provides three equally different ways on how this might happen. Firstly, people might underestimate individual energy use as well as its contribution to environmental problems. Secondly, by overestimating the prevalence of non-conservation as a habit shared by other people, suggesting this to be a normal, societal behaviour. Thirdly, by over-claiming the frequency of pro- environmental activities, such as recycling, as a way to support the feeling of personal contribution and reinforcing the perception of already doing everything they can, (Cialdini et al., 1990; van der Pligt, 1985.) An alternative persuasion theory that might be applied is, Higgins’s (1987) Self Discrepancy Theory, that assumes that the individual self-concept is derived partly, from ones’ own perspective of ‘myself’ and partly, from ‘my’ perceptions of others’ perspectives of me. The theory distinguishes between six distinct types of self-concept: actual-own, actual-other, ideal-own, ideal-other, ought-own and ought-other, with discrepancies giving rise to different types of emotional response. For example, discrepancy between ‘my’ actual self-concept and ‘my’ ideal self-concept is likely to give rise to dejection-related emotions, such as disappointment and dissatisfaction. Discrepancies between ‘my’ actual self-concept and the ideal concept others have of me, on the other hand, are most likely to give rise to feelings of shame or embarrassment. Incongruities between ‘my’ actual self-concept and ‘my’ ought self-concept are likely to give rise to feelings of guilt. Social judgment theory, (C. W. Sherif, Sherif, & Nebergall, 1965; M. Sherif & Hovland, 1961), is another persuasion theory that might be used and that assumes that people make evaluations, so called judgments, about the content of messages based on their anchors on a particular topic. When the topic is one that has personal significance to the individual, it is considered to be central to their sense of self, hence, they are ego-involved, (Dainton & Zelley, 2005). The theory suggests that each person’s attitudes can be placed into one of three categories, with the individual reaction to a persuasive message depending on the position on the topic, (M. Sherif & Hovland, 1961): (1), the latitude of acceptance, includes all those ideas that people find acceptable (2), the latitude of rejection, includes all those ideas that people find unacceptable and (3), the latitude of non-commitment, includes those ideas for which people have no opinion. Social judgment theory proposes that persuaders must carefully consider the pre-existing attitudes of an audience before
  • 77. 4. Energy use and intervention strategies 57 designing the message. According to the theory, three scenarios can take place: (1), sending a message that falls into people’s latitude of rejection might lead to unsuccessful, persuasive effort, (2), sending a message aimed at people’s latitude of acceptance might only lead to reinforcement of what people already believe, rather than persuasion, or (3), sending a message targeted to people’s latitude of non-commitment, or the edges of it, would be true persuasion, (Dainton & Zelley, 2005; Miller, 2002). A further persuasion theory that could be applied, is the elaboration likelihood model, (Petty & Cacioppo, 1986), that predicts that if listeners are motivated and able to consider an elaborated message, persuaders should rely on strong, factually based arguments and that arguments can backfire if they are weak, or poorly presented, (Dainton & Zelley, 2005). Conversely, persuaders should focus on emotionally based peripheral messages if receivers cannot, or will not, consider an elaborated message, even though recognizing that using a peripheral route is expected to guarantee no long-term change, but rather minimal and transitory effects, (Petty & Cacioppo, 1986). As can be seen, there are numerous persuasion theories and while each of them varies in their respective approach, they all might be applied to promote behavioural change and as will be further examined in Chapter 8, once it comes to perceived requirements (RQ3a) and individual perceptions on the effectiveness of intervention strategies (RQ3b). 4.2.1 Persuasion and communication Persuasion is often associated with communication and behaviour change intervention. Literature suggests that unpopular messages, such as the need to change lifestyles and to reduce consumption, may be rejected, or ignored, to avoid confronting the implications for appreciated behaviours, (Feinberg & Willer., 2010; Upham et al., 2009, van der Pligt, 1985). Thus there might be the need for creating a new balance by changing individual attitudes rather than behaviour, (Gass & Seiter., 2003). As such attempts to shame individuals into adopting pro-environmental behaviours can be ineffective in changing behaviours, (O’Keefe, 2002); any type of persuasion attempt should be framed in a way to build up narratives to which individuals can connect. Altogether, this implies that any type of message that refers to potential solutions should be
  • 78. 4. Energy use and intervention strategies 58 delivered in a positive, and not confrontational frame, therefore encouraging individuals to believe in their ability to contribute to what they perceive as a positive change. 4.2.2 Mental models and communication Individuals use their knowledge and beliefs to help them interpret new information in order to reach conclusions. A mental model represents a person’s thought process for how something works and serves as the framework to fit new information, (Morgan, Fischhoff, Bostrom, & Atman, 2002). Mental models are often based on incomplete facts, past experiences and even intuitive perceptions, that help shape actions and behaviour, influence what people pay attention to and define how people approach and solve problems, (Carey, 1986). But, by working as a framework, sometimes a mental model may also work as a filter, resulting in only selective knowledge being considered, with people seeking out, or absorbing, the information that only matches their mental model. Here, they might be confirming what they already believe about an issue, which then could pose a potential challenge for communication aiming at promoting more energy efficient behaviours. This situation is known within the literature as a confirmation bias, as people look for information that is consistent with what they already think, want, or feel, leading them to avoid, dismiss, or forget information that requires them to change their position and, quite possibly, their behaviour, (Shome & Marx, 2009). It might be thus that once people say, “I can’t”, that it simply means, “I don’t want to”. Thus an important criterion for effective communication is to know the audience, what they understand and misunderstand about the issue, how they perceive a threat to their current and intended behaviours, their values, beliefs and policy preferences, or their barriers to change and underlying motivations. All of these could either constrain, or inspire, further engagement with solutions, (Maibach et al., 2009). Practitioners thus need to discover what misconceptions the audience may have in their mental models, so that information can be actively communicated with appropriate language, metaphor, and analogy, i.e. combined with narrative storytelling, made vivid through visual imagery and experiential scenarios, balanced with scientific information and delivered by trusted messengers in group settings, (Shome & Marx, 2009). Framing is thus perceived as the setting of an issue within an appropriate context to achieve a desired interpretation, or perspective. In addition, to frame the message, practitioners also need the specifics of the target audience and their segmentation, in order to prepare frames in advance to fit with the audience mental models, (Shome & Marx, 2009). To be successful, messages might also consider
  • 79. 4. Energy use and intervention strategies 59 individuals’ goals and whether their goal is to make something good happening, or preventing something bad from happening, (Shome & Marx, 2009). 4.2.3 Behavioural change, and relevant and supportive communication Humans hold a limited capacity for worrying; they have a finite pool of worry, (Linville & Fischer, 1991), therefore tending to view near-term threats as more relevant and of greater urgency than caring about future problems, (Slovic, 2000; Slovic et al., 2004; Weber, 2006). People thus tend not to immediately react to threats that may manifest themselves in the distant future, but rather look for balancing long-range worries with the demands of more immediate concerns, (Chaiken & Trope, 1999; Marx et al., 2007). The literature suggests this to be one of the barriers to motivate people into taking action to prevent environmental problems, (Shome & Marx, 2009). In addition to this, individuals have a natural tendency to avoid losses, rather than to seek gains, (Kahneman & Tversky, 1979). Once a, ‘gain vs. loss’, frame is combined with a, ‘now vs. future’, frame, people discount future gains more than future losses, (Thaler, 1981). For example, people may be more likely to adopt environmentally friendly behaviours if they believe their way of life is threatened and that inaction will result in even greater threats, thus addressing people’s desire to avoid future losses rather than realizing future gains. They might be less likely to adopt these measures if they focus on the current situation, which they see as acceptable and discount future improvements of it. Thus any type of communications should be relevant and supportive. Shome & Marx (2009), provide an example for such relevant and supportive communication by promoting energy efficiency appliances as helping the homeowners to avoid losing money on higher energy bills in the future, instead of helping them save money in the future. 4.3 Structural interventions As can be seen in Figure 4-5 (p.50), there are a number of intervention types that can be grouped in between structural and psychological interventions, (Poortinga et al., 2004; Steg, 2003). Structural interventions aimed, for example, at changing the (social), context in which behavioural decisions take place (Fig. 4-5), are based on the belief that by altering the conditions in which behaviour takes place,
  • 80. 4. Energy use and intervention strategies 60 behaviour will change accordingly (Fig. 4-5). Structural interventions include, for example, financial- economic measures, physical/technical alternatives, and legal regulation, (Steg, 2003). 4.3.1 Financial-economic interventions Financial-economic measures hold the potential to promote energy saving by making energy-intensive behaviours relatively more expensive and environmentally-friendly alternatives relatively less expensive. To illustrate, increasing the costs of energy use, by means of a tax on gas and electricity, may induce households to reduce their energy use, (Streimikiene & Ciegis, 2010). Furthermore, increasing the prices of products that require much energy may encourage households to choose less energy-intensive alternatives. Nevertheless, these kinds of measures only tend to be effective if consumers take the financial cost into account when making such choices. 4.3.2 Physical/technical interventions Physical/technical alternatives involve changes to already existing infrastructure and equipment, such as the introduction of energy-efficient appliances. There is some overall agreement that efficiency improvements are necessary for sustainable development, but nevertheless technological innovations are perceived as a partial solution, as the effectiveness of technological measures requires the adoption of new technology, as well as the knowledge of how to use such technologies efficiently, (Abrahamse, 2007; Steg, 2003). In addition to this a possible rebound effect, as identified by Khazzoom (1980), may also occur, in that consumers may increase the use of efficient appliances, thus counterbalancing initial efficiency gains. 4.3.3 Legal regulation Also there is legal regulation as entailed by the introduction of legislation by the government, such as speed limits for cars in order to reduce carbon dioxide emissions. Often this form of measures is associated with some form of punishment to those whose behaviour deviates from the regulations and is based on the assumption that these rules will eventually become internalized. Regulatory measures may be an effective strategy for behavioural change, provided the monitoring and enforcement system works properly.
  • 81. 4. Energy use and intervention strategies 61 4.4 Psychological interventions In contrast to structural interventions, psychological interventions aim to change existing perceptions, knowledge, attitudes, norms and values (i.e. individual-level variables), so that behaviour will change accordingly, (Southerton et al., 2011). A recent review of the potential of structural and psychological intervention strategies has proved that the most promising approaches involved energy audits, community based interventions and the combination of more than one type of intervention, and producing savings of between 2 and 20 percent, depending on the type of intervention, (EEA, 2013). There are a number of models that attempt to support psychological intervention, such as the three term contingency ABC 11 (Antecedent-Behaviour-Consequence), model of behavioural change, (Geller, 2002), that assumes that behaviours are directed by antecedent stimuli that preceded them and that state the availability of a positive, or negative, consequence, (Dwyer, Leeming, Cobern, Porter, & Jackson, 1993; Geller et al., 1990; Lehman & Geller, 2004). Antecedent-Behaviour interventions attempt to influence one or more determinants prior to the performance of the determinant behaviour. Examples of antecedent interventions such as commitment, goal setting, modelling and information, (Abrahamse et al., 2005) aim at influencing underlying behavioural determinants (e.g. knowledge). On the other side of the ABC model are Behaviour-Consequence interventions, which are based on the assumption that once positive or negative consequences are attached to certain behaviour, this will subsequently lead to an alteration of this behaviour, (Geller, 2002). Within the environmental context this implies, for example, that pro- environmental behaviour becomes a more attractive alternative, once positive consequences, such as monetary incentives, are attached to it. Feedback and rewards are another possible Behaviour- Consequence strategy. For instance, once households receive feedback about their efforts to reduce energy use, they may, as a result of the positive consequences attached to their behaviour, be motivated to further conserve energy since they might have become knowledgeable, (Geller, 2002). Savings have been shown in the region of 5 – 15 percent for direct feedback and 0– 10 percent for indirect feedback, (Darby, 2006). Recent research on smart metering and householder engagement has, however, equally found that feedback alone is not enough to interest occupants, (Darby, 2010). 11 Not to be confused with the ABC behavioural change model developed by Stern et al (1995)
  • 82. 4. Energy use and intervention strategies 62 Following, a number of such psychological intervention approaches will be discussed. 4.4.1 Information provision Providing information aims to increasing knowledge regarding energy use, which in turn is expected to result in the adoption of more energy efficient behaviour, (Geller, 2002). This assumption of information provision as a predecessor of behaviour can be grounded in the Knowledge Deficit Theory (KDT), a theory that advocates for a causal relationship between knowledge and behaviour, (Schultz, 2002). KDT’s primary assumption is that people want to help themselves and the environment, but they lack information about how and/or why they should make changes to their behaviour. As such, the provision of information about how, or why, one should act would help overcoming inaction and lead to the desired behaviour. From the literature it is, however, not entirely clear whether this cause-effect is indeed taking place and that information regarding energy saving measures is leading to a reduction of energy use. This cause-effect relation might be, for example, negatively impacted by limited time and capacity to process all the available information, or because insight alone does not necessarily change behaviour, or since the subject of energy use might be too complex to be changed by single, stand-alone interventions, such as information and feedback provision. Information provision, as a way to increase individual awareness of problems related to energy use, as well as to increase the knowledge about possible alternatives, has been widely used for promoting energy saving and conservation behaviours, (Abrahamse et al., 2005). In the spheres of policy and the energy research community, the information deficit model tends to dominate, (Janda, 2011). The provision of information, or feedback, is perceived as a way of ‘teaching’ people the required energy management skills and in giving people a sense of their ability to control energy use, (Chatterton, 2011). Information provision covers a large spectrum of interventions, mass media campaigns, information and training centres, technical manuals and brochures, labelling and energy audits, and can be used for providing detailed information to various actors, consumers, equipment operators/technicians, managers of building complexes, engineers, architects and decision makers, (BPIE, 2011). Individuals are often presented with a number of suggested
  • 83. 4. Energy use and intervention strategies 63 pro-environmental behaviours in the form of, ‘To Do’ 12 lists, which are unranked lists of recommended actions which aim to provide some guidance and help to individuals having an understanding of the type of pro-environmental behaviours they could adopt, (Gardner & Stern, 2008). It has been observed however, that such guidance and ‘To-do’ lists could equally lead to individuals deciding to take no action at all, or to only carry out one or two actions, or perhaps, to engage with those actions that are the easiest to remember and perform, regardless of the environmental impact those actions might have, (Barr & Gilg, 2006; Darnton, 2008; Gardner & Stern, 2008). Information campaigns are also found to be cost efficient and an easy to implement means to overcome information barriers, though the literature equally found that information campaigns often have little, or no, impact on promoting behavioural change and thus can be expensive in relation to their effectiveness, (McKenzie-Mohr, 2000; Southerton et al., 2011). Evidence suggests that information alone is seldom sufficient to promote change, (Abrahamse et al., 2005; Geller, 2002; Staats et al., 1996). Yet, in cases where lack of knowledge has been identified as a barrier to participation, information dissemination seems to motivate changes in behaviour, (Geller, 2002). Nevertheless, research also found that people often possess the knowledge required to engage in modifying behaviour, but they lack the motivation for doing so, which indicates the existence of an, ‘information-behaviour gap’, between the held information and behaviour, (Geller, 2002; Jackson, 2005; Prochaska, DiClemente, & Norcross, 1992; Schultz, 2002; Southerton et al., 2011; Stern, 1999). One example for such an information-behaviour gap is Al Gore’s film, ‘An Inconvenient Truth,’ that emphasized the seriousness of the global climate crisis, argues that it could be solved with present and foreseeable technology, and concludes that all citizens could play a meaningful role in the solution, thus creating a sense of awareness regarding the need for change for the better. Research found that watching the movie increased knowledge about the causes of global warming, concern for the environment and willingness to reduce greenhouse gases, but this willingness didn’t necessarily translate into action, (Gardner & Stern, 2008; Nolan, 2010). A review of intervention studies on household energy 12 To Do lists come in a number of formats: ‘20 things you can do’ http://www.ecomall.com/greenshopping/20things.htm ‘101 Ways To Heal The Earth’ http://www.context.org/ICLIB/IC22/Guide.htm ‘100 Ways to Save The Environment http://www.seql.org/100ways.cfm
  • 84. 4. Energy use and intervention strategies 64 conservation carried out by Abrahamse et al. (2005), provided some further evidence for the existence of an information-behaviour gap. They found that workshops, mass media campaigns and even targeted information provision in general led to higher levels of concern about the energy crisis, to an increased level of knowledge about energy conservation, of (self-reported), conservation behaviours and to stronger intentions to adopt energy-saving measures. However, even though information might have influenced the underlying determinants of energy use, Abrahamse et al. (2005), found no clear evidence that this also resulted in any reduction in energy use. The literature does provide, however, some evidence that information provision could support the adoption of more energy efficient behaviours. Information provision might support the adoption of energy efficient behaviours when used in combination with other type of intervention, such as feedback provision, or auditing and personalised advice, (Abrahamse et al., 2005). Equally, information strategies that made use of, for example, face-to-face interventions, which used feedback mechanisms such as monitoring equipment (water or energy), or that included individual pledges to a long term commitment to reduce consumption, seemed to support the adoption of energy efficient behaviours, (Southerton et al., 2011). For example, Staats, Leeuwen, and Wit (2000), found that office workers improved their energy efficient behaviours, such as keeping thermostat settings consistent and removing objects from heating grates, immediately after an informational brochure was handed out to them. Subsequently, other intervention components, such as poster prompts and feedback, were added to maintain these energy efficient behaviours. The results of these subsequent intervention components demonstrated that energy efficient behaviours benefited from the combination of different strategies. Secondly, information provision might also be more effective if such information-based interventions are tailored to fit specific situations, (Abrahamse et al., 2005). Tailored information is highly personalized and specific information. An advantage of this approach is that people, instead of getting an overload of general information, which may not apply to their situation, receive tailored information only. Examples of tailored information are energy audits, i.e. a home visit by an auditor who supplies a range of energy-saving options based on their current situation. For instance, auditors may advise a household to apply insulation and/or to lower thermostat settings as well as a complementary set of curtailment behaviours, (Abrahamse, Steg, Vlek, & Rotehengatter, 2007). Previous research shows that home energy audits (mainly focusing on heating and air conditioning), might
  • 85. 4. Energy use and intervention strategies 65 be a very efficient intervention measure to increase energy savings in households, (Abrahamse, 2003, 2007; Leiserowitz et al., 2009). Thirdly, tailored information, targeted at an intended population segment, also appeared to support the adoption of energy efficient behaviours, (Leiserowitz et al., 2009; Southerton et al., 2011). Successful information campaigns seem to use practices that are nowadays commonly accepted as good campaign design practices: simple, clear messages, repeated often through a variety of interpersonal and media channels, by a variety of trusted sources, (Streimikiene, 2012). 4.4.2 Commitment and goal setting Commitment strategies involve asking participants to make a verbal, or written, commitment to perform a desired behaviour, such as to save energy, which is often linked to a specific goal or reference point, for instance, to reduce energy use by X percent, (Abrahamse et al., 2005). Goal setting is often used in combination with other interventions, such as feedback (to indicate how households are performing in relation to the goal), or as part of a commitment to conserve a certain amount of energy. Cialdini (2001), argued that once people have made a commitment, they are more likely to perform their target behaviour, especially, if the commitment is active, public, and perceived as voluntary. Commitment strategies might also draw on the social norm of consistency, which creates pressure to be internally and externally consistent, depending on whether the pledge was to oneself, or public, (Cialdini, 2001). Pledges to oneself may activate a personal norm, meaning a moral obligation, with public pledges activating social norms, the expectation of others to pursue the behaviour. Commitment strategies are often seen as a way to use the ‘foot-in-the-door’ technique that assumes that compliance to a first (smaller), request will result in compliance to a subsequent (bigger), request, (Abrahamse et al., 2005). The efficacy of commitment and goal setting in bringing about changes in energy use is expected to increase once used in combination with other type of interventions, (Abrahamse et al., 2005). For instance, commitment strategies that have been combining goal setting with feedback appear to be more effective than using goal setting alone, (McCalley & Midden, 2002). Commitment strategies have been, for example, successfully applied to reduce household energy use, especially in the long-term, as found in several studies, (Abrahamse et al., 2005). Similarly McCalley and Midden (2002), found that participants who had been given a goal as well as feedback, saved more energy per washing trial, than participants who had only received feedback (without a goal). In
  • 86. 4. Energy use and intervention strategies 66 addition to this, Becker (1978), highlighted the care one should have in defining goals. During this study, households were either given a relatively difficult goal (20 percent), or a relatively easy goal (2 percent), to reduce electricity use. The results suggest that an easier goal appears not to be effective, as a 2 percent reduction may be perceived as not being worth the effort. Finally, previous research found that there appeared to be no significantly different behaviour between participants who had been able to set a goal and those with an assigned goal, (Abrahamse et al., 2005; Becker, 1978; Bittle et al., 1979; Brandon & Lewis, 1999; Gerdes, 2009). In summary, commitment, goal setting and feedback appear to be viable mechanisms for reducing household energy use and, especially, in view of realising long-term behavioural changes, (Abrahamse et al., 2005); and particularly when used in combination, (McCalley & Midden, 2002). 4.4.3 Behavioural intervention through design As has been explored and demonstrated in previous sections, infrastructures and technologies are at the core of energy consumption, whether that is cooking, bathing or surfing the internet, but these also lock people into behaviours that can be very difficult to change, (Maréchal, 2010; Southerton et al., 2011), as has been shown in Chapter Two. Thus, behavioural interventions might make use of environmental design, or material context adjustments that focus on the introduction of devices, or objects, that create opportunities for a desired behaviour modification, such as pro-environmental behaviour, more salient, or convenient. This is also known as choice architecture and the concept of nudge, where the default options are set in order to facilitate the selection of the individual’s best choice, (Thaler & Sunstein, 2008), through changes in the context in which they are made. According to Grist (2010), nudging is of particular use to influence habitual behaviours. To facilitate better decision making in individuals, Nudge approaches can use product design as a mechanism to nudge behaviour in a particular direction in specific contexts. An example of nudging can be seen in Portland, USA, where the timing of traffic signals were changed in a way that was supposed to allow a reduction in petrol use by motorists, (Southerton et al., 2011). The Portland case thus illustrates how nudging can be used without individuals having to make a choice, or necessarily aware that they have been ‘nudged’. Another example of nudging is the default opt-in for discretionary charges to finance carbon offsetting schemes, (Southerton et al., 2011), or the default of a TV, or power box, from
  • 87. 4. Energy use and intervention strategies 67 stand-by to off. In this way, choice architecture can contribute to framing individual options by making it easier for people to adopt the desired rather than, the undesired behaviour, (Dobson, 2011; Thaler & Sunstein, 2008). Nevertheless, there are some critics to the nudging approach. For instance, Dobson (2011), argues that nudging fails to engage people at the level of principle and, could be considered as a paternalistic, anti-democratic approach to changing behaviour without prior knowledge. This will be further examined in Chapter 8 when it comes to perceived requirements (RQ3a) and individual perceptions on the effectiveness of intervention strategies (RQ3b). Dobson (2011), further argues that though nudging is perceived as a ‘low-cost’ and ‘low pain’ strategy, this actually might not necessarily be the case. Physical infrastructures are also an important design element, since they support the development of social context, of the norms of consumption and is prominent in energy, building, transport, water and waste/recycling sectors, (Southerton et al., 2011). Shove and Southerton (2000), provided one example with the introduction of the freezer within households, which has developed alongside an entire frozen- food infrastructure. This has resulted in changes to the design and use of houses and kitchens, the development of the out-of-town supermarkets and a subsequent decline of local food stores, which in turn render household food provisioning, without a freezer, increasingly difficult. Shifting infrastructure thus holds a significant potential to facilitate individual decision-making and to shift social norms toward more sustainable behaviours. As such, interventions in material infrastructures not only create the conditions for new habits to emerge, but they also hold the potential to lock people into sustained environmentally friendly behaviour. The main constraint with regards to intervention relates, consequently, to the infrastructure and cost involved in establishing those, as has been discussed in section 4.3.2. 4.4.4 Rewards and punishments Reward and punishment approaches appeal to people’s self-interest and can be effective in the short term. Individuals have an apparent natural tendency to avoid losses, rather than to seek gains, (Kahneman & Tversky, 1979). They discount future gains more than future losses, (Thaler, 1981), prefering to have short term gains rather than long term ones, (Nordlund & Garvill, 2002, 2003; Stern, 2000; Thøgersen & Ølander, 2002) and they tend to give preference to taking action where these create potential gains, rather than taking action to avoid potential losses, (Tversky & Kahneman, 1991). With this, the logic behind the reward
  • 88. 4. Energy use and intervention strategies 68 and punishment approach is simply to avoid pain (punishments) and embrace pleasure (rewards). As long as the incentives and disincentives are aligned with the goal, the adoption of different behaviours is evaluated as possible. Dobson (2011) highlighted two main benefit of this approach: it can work very fast, often resulting in observable positive outcomes as soon as a charge and incentive measure is put in place and, people do not need to agree with the environment agenda for it to work. Acceptance might be an issue in particular in the case of taxes, charges, or fees. As an example, a BBC World Service Poll (2007), survey showed that 50 percent of responders’ were in favour of raising taxes on energy sources that contribute to climate change, whilst 44 percent opposed this. Acceptance levels did, however, increase once it was noted that the revenues of those taxes would be devoted to improving efficiency and seeking out sources of energy that do not produce climate change, or if other taxes were reduced in line, so that the total tax bill remain the same. Less agreement seems to exist regarding the effectiveness of financial incentives. Southerton et al. (2011), highlighted that financial incentives often interfere with market mechanisms, supporting earlier findings from Thøgersen and Møller (2008) that illustrate that financial incentives do not necessarily foster long term changes in behaviour, once the incentive is removed. Even though there is evidence that rewards seem to have a positive effect on energy saving and have effectively encouraged energy conservation, there is less evidence that this is not a short-term effect and that desired behaviours are not dropped to baseline levels once the reward contingency is discontinued, (Abrahamse et al., 2005; Dwyer et al., 1993; Geller, 2002; Geller et al., 1982). Dobson (2011) suggested that a reason for such a reversal might be the fact that the strategy seems to fail to engage people at the level of principle, since with punishments and rewards, people do not need to have any environmental commitment whatsoever for it to work. This is to say that what initially could be perceived as a short-term advantage with immediate impact, can actually become a disadvantage in the long-run, due to the fact that people respond to the prompt and not the principles underlying it (Dobson, 2011). Nevertheless, Geller (2002), added to this discussion by suggesting that relapses can also result from interventions that were, relatively, short in duration and not in place long enough to lead to long-term behaviour change. In contrast, strategies geared towards punishment seem to have been more successful in enforcing change, such as monetary penalties discouraging unwanted behaviours, i.e. the London congestion charge. Nevertheless, this might be, again, of short-term impact, as (Dobson, 2011), studies of the London congestion charge have shown that after an initial period of traffic reduction, levels increased again. This relapse potential perhaps
  • 89. 4. Energy use and intervention strategies 69 also explains why, in recent years, less focus has been placed on environmental interventions that use reward schemes to incentivise change. During the 1970’s, reward over punishment strategies were a popular component of environmental interventions due to the negative attitudes and counter-control measures that can result from perceived punishment, (Brehm, 1972; Skinner, 1971). 55 percent of the interventions reviewed by Geller et al. (1982) involved the use of tangible rewards. In contrast, only 27 percent of the studies (15 of 54), from the 1980’s reviewed by Dwyer et al. (1993) used rewards, compared to 13 percent (4 of 32), of environmental related studies published since 1990. In summary, reward and punishment systems have an, apparent, positive and viable short-term impact but are less promising in the long-term, (Abrahamse et al., 2005; Dobson, 2011; Dwyer et al., 1993; Geller, 2002; Geller et al., 1982; Nordlund & Garvill, 2002, 2003; Southerton et al., 2011; Stern, 2000; Thøgersen & Møller, 2008; Thøgersen & Ølander, 2002). But, they might equally contribute to the disconnection of people thinking about the moral and ethical dimension of sustainability and thus reduce the potential for social learning within the process (Dobson, 2011). Rewards and punishments systems thus hold the potential to reduce the likelihood of sustainability being thought of in normative terms. Sustainability becomes a non-normative policy objective achieved by the mobilisation of a reductive view of human motivation (self-interested utility maximisation), without making reference to sustainability at all; so missing the principle and opportunities for long-term social learning. In addition to this, rewards and incentives might have a different impact depending on the household income. Household energy use is related to people’s income, with wealthier families spending more on energy than poorer ones (section 2.2.5.). This punishment and reward system might have differing impacts dependant on the different income groups and on how much is spent, as a fraction of income and/or expenditure and is likely to effects their reaction to such types of interventions. Finally, rewards and punishments systems do not, apparently, address the performance context of habits, (Maréchal, 2010), thus they do not seem to take into account one of the identified barriers to energy savings, as has been discussed in Chapter three. 4.4.5 Learning theories and modelling Modelling is a way to provide examples of desired behaviour to encourage learning by, trial and error and by observing how others behave, (Bandura, 1977b). Modelling thus assumes that examples will be followed
  • 90. 4. Energy use and intervention strategies 70 once they are understandable, relevant, meaningful and rewarding, in terms of positive results to people. Evidence regarding the use of modelling in energy conservation areas seems to be scarce. In studies from the 80s, Winett and Kagel (1984) and Winett, Leckliter, Chinn, Stahl, and Love (1985), demonstrated its utility in increasing energy saving and conservation at home, at least in the short term, with participants who viewed a 20-minute video presentation of conservation behaviours significantly decreasing their residential energy use by 10 percent over a nine-week period when compared to controls. Additionally, before and after testing revealed a significant increase in knowledge for the experimental group, but not for the control group. A follow-up study, one year later, showed, however, that the savings were not maintained, thus modelling intervention did not lead to a long-term behavioural change. More recently, McMakin, Malone, and Lundgren (2002), used videotaped modelling, as part of a multi-component campaign, to reduce home energy use of residents at military bases; this proved to be moderately effective in promoting behavioural change. 4.4.6 Social learning community based approaches Community-based initiatives appear to be well in line with social practice theory, (Giddens, 1984) and often seek to change consumer behaviour by influencing social norms, by focusing in on the importance of social networks for circulating information and expectations regarding appropriate behaviours. They seek to support individual efforts in order to live more sustainably by framing what it is that, ‘we’, like to consume, as well as what, ‘we’, understand to be appropriate, or inappropriate, conduct, (Southerton et al., 2011). Within this structure, community based initiatives target behaviour, followed by careful analysis of the barriers that prevent the desired behaviour, leading to the piloting of a community-wide intervention plan, within a small segment of the community and finally, to the implementation and evaluation of a community-wide application, (McKenzie-Mohr, 2000). Thus, the objective is to help reduce the gap between current intervention strategies and to optimize the conditions to enable individuals to carry out energy efficiency behaviour. Namely (1), people value energy efficiency measures more if the benefits remain directed to themselves; (2), energy use and savings must be visible; (3), goals and motives for energy efficiency measures must be provided; and finally (4), information must be personalized and presented in a clear way, (McMakin et al., 2002). One example of Community-based initiatives is the
  • 91. 4. Energy use and intervention strategies 71 EcoTeams Program (ETP) that consists of small groups, e.g. neighbours, friends and families, who come together once every month to exchange information about energy-saving options, (Abrahamse et al., 2005) and to receive feedback about own and other EcoTeams energy saving practices. Staats, Harland, and Wilke (2004), suggest ETP could be a promising type of intervention, since it has been successful in reducing energy use in several domains, both shortly after the program and during a follow-up two years later. However and as already mentioned, due to the combined set of interventions that is often used within ETP, it is difficult to attribute success to a single intervention domain, (Abrahamse et al., 2005). Furthermore, ETP participants presumably were highly motivated, making it difficult to generalize results to wider populations which might be holding different levels of motivations regarding energy use and energy saving behaviour, (Abrahamse et al., 2005). 4.5 Combined Structural/Psychological interventions Some interventions identified within the literature, which appear to be a rather combined approach of structural and psychological interventions, follow on below. 4.5.1 Prompting strategies Prompting strategies are verbal or written messages that designate desirable target behaviours and prompting messages are considered to be a way to provide information, (Staats et al., 2000). Prompting strategies might be an attractive intervention, since they can be of relatively low cost and can have considerable impact if used properly. In accordance to Geller, Winett, and Everett (1982), prompting strategies should meet a number of conditions so as to maximize their effectiveness, namely that the target behaviour should be easy to perform, clearly defined and that the message is displayed, in close proximity, to where the target behaviour can be performed. In addition to this, messages should be stated politely to avoid eliciting negative reactions, (Brehm, 1972; Skinner, 1971) and labelled in such a way as to provide information designed to help consumers make informed choices, (Shove, 2004). To further increase effectiveness, products would need to be fully and consistently labelled so as to provide consistent and comparative levels of information for consumers, (DGGE/IP-3E, 2004). The general challenge for carbon
  • 92. 4. Energy use and intervention strategies 72 labelling is to ensure that the information provided within the label is meaningful, easy to understand, standardised, and that motivates consumers into wanting to take action, (Southerton et al., 2011). 4.5.2 Feedback provision Feedback involves providing information to participants about their environment-relevant behaviours and is thus similar to information provision. A distinctive difference to information provision is that feedback strategies tend to be more tailored so to make the consequences of behaviour more salient. Feedback in the energy use area could be, for example, to provide households with information about their energy consumption, or achieved energy savings, with the expectation that households can associate certain outcomes, e.g. energy saving, with their behaviour, (Abrahamse et al., 2005). In most homes, attempts to understand energy use have been, aptly, compared to shopping at a grocery store without any prices on display and receiving a bill at the end of a month’s worth of purchases, (Kempton and Montgomery, 1982, Janda, 2011). Feedback might vary in frequency, purpose and type, (Darby, 2006; Fischer, 2008). First of all, the frequency of feedback is associated with the way feedback is provided, e.g. monitoring devices can provide continuous feedback, compared to energy bills, which provide feedback, perhaps, on a monthly base. Secondly, feedback can also be provided for specific households or, as a comparison to other, similar households, neighbours, or communities. Feedback about individual performance relative to others may be helpful in reducing household energy use by the mediation of social norms, by comparison of their energy use to that of friends, or neighbours, (Cialdini et al., 1991; Cialdini et al., 1990; Triandis, 1977). Comparative feedback could thus influence the perception of what constitutes ‘normal’ energy use and also produce a feeling of competition, social comparison, or social pressure, which may be especially effective once important, or other relevant factors are used as a reference group, (Steg, Dreijerink, & Abrahamse, 2006). Yet, evidence appears scarce that using comparative feedback could indeed be more effective than individual feedback, (Brandon and Lewis, 1999). This impact might also be influenced by the way comparative feedback is provided. This is to say that when people become aware of a social descriptive norm (what is done), their behaviour tends to change to become closer to the norm, which could then negatively impacting those users that use less energy, as they might feel tempted to increase their energy use, (Brandon & Lewis,
  • 93. 4. Energy use and intervention strategies 73 1999). The power of these messages can nevertheless be harnessed by using injunctive norms instead, with messages conveying approval of particular actions considered to contribute to decrease the effect, (Schultz, Nola, Cialdini, Goldstein, & Griskevicius, 2007). Thirdly, it is not clear whether it makes any difference to give feedback in terms of monetary rather than environmental costs, since studies investigating this difference did not find any evidence for this, or determination as to which could be more meaningful to recipients, (Brandon & Lewis, 1999). 4.5.3 Monitoring systems and metering The ‘invisibility’ of energy might contribute to individual unawareness of consumption levels and fostering support towards measures, such as feedback on energy consumption and personal contribution, could provide an access to the problem of providing information, (Darby, 2006; Roberts & Baker, 2003). Monitoring systems, such as energy meters, could be seen as a way to, ‘commoditize,’ behaviour into a good proxy, in order to make consumption visible, (WWF, 2008). Today's monitoring systems offer new opportunities to observe and give feedback to people and to engage with them, in real time, about the complex ways in which they consume energy. They are however not entirely new and smart metering, for example, was initially proposed in the 1970s, though only recently has come into full view, (Darby, 2010). Recent research on smart metering and householder engagement agrees that feedback alone is not enough to interest occupants, (Darby, 2010), but nevertheless, feedback strategies have shown modest, but consistent, energy savings, although some exceptions do exist, (Abrahamse et al., 2005; Dwyer et al., 1993; Geller et al., 1982). Research shows that in-home displays give interested users feedback information to help them understand and manage their electricity more efficiently, achieving savings in the range of 5–15 percent, (EEA, 2013). There is also evidence that displays have an enduring impact, even if only used for short periods, through changed habits and investment in efficiency measures, (Darby, 2006; Rossini, 2009). Monitoring systems have been shown that feedback efficacy is expected to be influenced by the time that the feedback is provided; and favouring feedback provision immediately after the behaviour occurs, (Geller, 2002). The more frequent that feedback is given, the more effective it is with the most positive effects being observed with continuous feedback, (Abrahamse, 2003; Abrahamse et al., 2005). However, the use of energy meters has been under discussion since their acceptance and impact levels, apparently, do vary. On
  • 94. 4. Energy use and intervention strategies 74 one side, appreciation could be observed, but equally there had been annoyance, (Hargreaves, Nye, & Burgess, 2010; IPPR, 2009). In addition to this, the impact of energy meters, in terms of energy saving, is considered to decrease with time (EEA, 2013) which is in-line with findings from Darby (2006), that feedback on consumption could have an impact, but might not be sufficient for people to understand and thus change their behaviour regarding energy saving. Yet, the joint use of feedback and commitment could be a viable way to achieve impact, (Maréchal, 2010; Stern, 2000). 4.5.4 Social marketing Social marketing can be defined as the application of marketing principles and tools to achieve socially desirable goals, (Andreasen, 1995; Kotler & Zaltman, 1971). Social marketers understand that behaviour change is the main goal and that to change behaviour it is not necessarily required to change people’s fundamental attitudes and beliefs, but rather to work within their current attitudes and beliefs. As such social marketing opens the opportunity to promote behavioural change based on existing values that are not necessarily pro-environmental, but still could foster more sustainable behaviours, (Southerton et al., 2011). Social marketing has been used in a variety of areas to promote individual behavioural change and, in particular, to provide solutions in public health areas, (Grier & Bryant, 2005; Helmig & Thaler, 2010). Social marketing generally promotes voluntary behavioural change based on building beneficial exchange relationships with a target audience for the benefit of society, (Schwartz, B. in Hastings, 2008). This draws from the exchange theory, (Hastings & Haywood, 1991), which states that people change their behaviour because they are offered something in exchange that, they perceive, provides greater benefits and fewer barriers than the alternative. As a result individuals will take action to adapt as it is in their interest and ability to do so. That is, they will take measures where the benefits outweigh the costs to them. As such, promoting individual change requires an understanding of some of the relevant principles which are the core of social marketing: the target population, segmentation of the population and aligning change interventions to specific segments. With this, the principle of change is clearly distinct from the regulatory, or the education principle, (Andreasen, 1995), as the regulatory principle focuses on rewards and punishments, while the education principle assumes that people modify behaviour as they acquire information or skills that they did not previously have. Voluntary behavioural change also means that there
  • 95. 4. Energy use and intervention strategies 75 is no coercion and as such, it does not exclude the Nudge approach, since changing the conditions in which behaviour occurs is not viewed as coercion as individuals are allowed to choose. Contrarily, choice architecture should rather be seen as a tool for making the ‘right’ individual decision as easy as possible for people to do. The history of commercial marketing shows that knowing and segmenting one’s audiences is a precondition for success. Behavioural change interventions that are drawing on social marketing thus need to be targeted at specific segments of the population. For example, in the case of adopting more energy efficient behaviour one would have to take into consideration the existing needs, barriers and motivations to save energy, actions already undertaken and those that individuals intend to take and accurately targeting segments, using messages, messengers, communications channels and policies that are appropriate to them, (Leiserowitz et al., 2009; Southerton et al., 2011). Whilst similar to commercial marketing, social marketing works on the principle of population segmentation using the 4Ps (product, price, place and promotion). These are the basic structural elements that social marketing addresses to produce a competitive benefit for a particular segment of the audience, once orientated through the market exchange filter, (Grier & Bryant, 2005; Weinreich, 1999), aimed at changing individual behaviour and attitudes, (Andreasen, 1995; G. Hastings & Saren, 2003; Helmig & Thaler, 2010; Kotler et al., 1989). The basic idea is to rebalance the 4Ps mix compensating for missing or weak Ps. The difference between commercial and social marketing is in what the 4Ps stand for. For social marketing the 4Ps have the following objectives: • ‘Product’ means the social proposition, the desired behaviour one is asking the audience to adopt, the associated benefits of adopting the desired behaviour and any tangible objects, or services, which support, or facilitate, the desired behaviour. • ‘Price’ means the cost of involvement and also the barriers that the target audience needs to face once changing towards the desired behaviour. Non-monetary costs such, as time, should also be considered. Here is where the exchange principle is important, since the benefits of changing behaviour should be greater than the costs.
  • 96. 4. Energy use and intervention strategies 76 • ‘Place’ stands for accessibility, either the location where the target audience will perform the desired behaviour, or where the product, or service, is made available to the target audience. • ´Promotion’ covers communication, how the product, or service, is made known to the target segment. For the energy area, the product is rather the adoption of new behaviour regarding the usage of energy consuming appliances and actions and not just of purchasing new appliances, (Peattie & Peattie, 2003). The academic literature on social marketing, behaviour change, and even commercial branding, suggests that people are motivated to purchase products and/or change their behaviour based on three broad categories of benefits, (Leiserowitz et al., 2009). These are; (1), functional benefits: what the product, or behaviour, will do; (2), self-expressive benefits: what the product, or behaviour, says about one; and (3), self-evaluative benefits: how the product, or behaviour, makes one feel about themselves. Leiserowitz et al. (2009), further proposed that functional benefits are ones that are relatively simple to promote and that promotional communication campaigns need only to invoke the functional benefits of the product, or behaviour that members of the target audience find most persuasive. On the other side, self-expressive and self-evaluative benefits, though being more challenging to promote, are often more powerful and of longer duration. Enhancing the functional benefits of saving energy could therefore involve messages such as, ‘It will save me money’, as those seem to be at the centre of individual motivation to save energy. Enhancing self-expressive benefits, on the other hand, might involve messages such as, ‘I’m the kind of person who cares about helping to reduce global warming’, while, associated self-evaluative benefits might including, ‘I feel good about myself once I do this because it’s the moral thing to do’. Judging from the literature, there appears to be, however, three limitations to the use of social marketing in the energy area. Firstly, a relation between the success and failure of behavioural change interventions could be influenced by the ability to remove barriers that currently impede target audience members from performing recommended behaviours, (Leiserowitz et al., 2009). As such, enhancing individuals’ motivation to change is necessary, but likely won’t be sufficient alone and in order for the recommended behaviour to be widely adopted, there will also be a need to remove the barriers that individuals face. In Chapters 2 and 3, a number of such barriers towards more pro-environmental behaviour, more specifically towards less
  • 97. 4. Energy use and intervention strategies 77 energy intensive ones, have been discussed and removing those barriers was seen to require addressing cultural, normative and individual psychological variables that are often hard to change. Secondly, the social marketing approach might actually serve to defer, or even undermine, the prospects for more far-reaching and systemic behavioural changes that are needed in the area of energy consumption. According to the WWF (2008), this is to say that social marketing might lead to feelings of uncertainty, despair and guilt, contributing to states of denial, paralysis and apathy resulting in people feeling helpless in regards to adopting more energy efficient behaviour, as discussed within section 3.4.3. Thirdly, in the case of energy, there might be no visible, direct benefit of saving energy. It is difficult for individuals to perceive the benefits of the social good that social marketing intervention promotes. As such, the use of social marketing within the energy consumption area might look for inspiration in other related areas, such as reducing the number of non-voters during elections, or donation campaigns. Kotler et al. (1989), recognized, for example, that social marketing campaigns could have limited success in promoting behavioural change, since individuals, even if aware of the consequences of their behaviour, might lack motivation, or ability, or simply because the competitive behaviour is more attractive. 4.6 Concluding remarks As has been discussed throughout this chapter, achieving lasting behavioural change might be a difficult undertaking, in particular since environmental values, beliefs and attitudes apparently do not have any significant influence on energy consumption. It can also be seen that there are a number of frameworks that attempt to support intervention strategies, by trying to find the right interplay between the various strategies each showing a slight variation in terms of existing factors and approach. This includes the right interplay between contextual factors and micro-level factors, plus a diversity of other determinants, motivations and barriers that may need to be taken into account for any successful intervention attempt. It has been discussed that there are a number of potential intervention layers and that any type of intervention might also have to take into account the role of communication and persuasion, so that the credibility of the sender, the persuasiveness of the argument/message, or the responsiveness of the audience can be assured. The literature shows a diversity of existing intervention strategies and types that could be broadly grouped into either, structural or, psychological interventions. While structural
  • 98. 4. Energy use and intervention strategies 78 interventions aim to change the (social), context in which behavioural decisions take place, psychological intervention aims at changing existing perceptions, knowledge, attitudes, norms and values (i.e. individual, micro-level variables). To date however, most intervention strategies have predominantly focused on voluntary behavioural change, rather than on changing contextual factors aimed at determining individual decisions. The difference here is, that contextual factors set the context where individual decisions are made and intervention strategies that include both, voluntary behaviour change and contextual factors, might, therefore, increase the level of success in promoting lasting behavioural change. Despite a growing body of research and evidence, there still appears to be no clear evidence for the potential long-term effectiveness of change interventions within the field of home energy use which this research attempts to explore further in Chapter 8. In regard to this, it can also be seen that there are numerous persuasion theories that might be applied to promote behavioural change, with each one providing a different approach that could be useful. Chapter 8 will thus investigate how such possible approaches, factors and determinants might be best considered within interventions (RQ3b) and what these requirements might be (RQ3a).
  • 99. 5. Research methodology and design 79 5 Research methodology and design This chapter discusses the methodological approaches taken in the research study. It also considers other theoretical applicable methodologies and reasons for discounting these approaches. The chapter provides an overview of the research design, the methods used to address research questions and details how research questions have been derived from previous literature review chapters. An overview of the research design is shown in Figure 5-1 outlining the relation between the different phases of research. Figure 5-1: Research design from initial framing to implementation. This research is of an exploratory nature and aims to explore how the adoption of more energy efficient behaviours at home could be encouraged. With this the research has the objective to gain an understanding of energy use at home and how the adoption of more energy efficient behaviours could be promoted. The methodological approaches chosen for this study thus must be compatible with the exploratory nature of the research and to support answering the overall research questions: • RQ1: What explains energy use at home? • RQ2: What influences energy use at home?
  • 100. 5. Research methodology and design 80 • RQ3: How to promote energy efficient behaviour? As can be seen from the questions, this research does not attempt to test existing theories, but to obtain an insight and in-depth knowledge, of the topic under investigation through the different phases of research. The study targets both energy users and energy conservation intervention practitioners in the area of energy efficiency, so to provide a more comprehensive and complete overview of potential behavioural interventions that would result in the adoption of more energy efficient behaviour. 5.1 Literature review on available methods The methodological approaches chosen for this study have been selected based upon the exploratory nature of the research and after careful evaluation and consideration of the possible theoretical applicable methodologies that are available. 5.1.1 Inductive or deductive Through this research a preference has been given for inductive research, with the emphasis on an exploratory approach to improve the understanding of energy use at home and how the adoption of more energy efficient behaviour could be promoted. In an inductive approach theory is developed from the observation of empirical reality; which involves moving from individual observation to statements of general patterns, or laws, (Hussey and Hussey, 1997). This is in contrast to a deductive approach where a conceptual and theoretical structure is developed and then tested by empirical observation, so to move from the general to the particular, (Hussey and Hussey, 1997). Empirical research requires choosing between the deductive or inductive research paradigms. Figure 5-2 demonstrates the differences between these two paradigms and research approaches. Figure 5-2: Inductive vs. deductive research approaches, (Rudestam, Newton, 2001, p.5).
  • 101. 5. Research methodology and design 81 As this research has been placing an emphasis on an exploratory approach an inductive approach has thus seen to be more appropriate to improve the understanding of energy use at home and how the adoption of more energy efficient behaviours could be promoted. 5.1.2 Subjective or objective Another decision that had to be taken relates to the question of subjectivity and objectivity, which means the extent to which the researcher is subjective (involved in or has an influence on the research outcome) or objective (distanced from or independent) in the execution of the fieldwork (empirical work). Easterby- Smith et al. (2002) and Tashakkori & Teddlier (2003) both discussed the traditional assumption that in science the researcher must maintain complete independence if there is to be any validity in the results produced. However, within this research, the researcher seeks to explore and understand the narratives built around energy use at home, uncovering the perceptions of reality, which is by its very nature, subjective. It is accepted that such a subjective approach, as used in the research, requires the recognition of any influence or limitation such subjectivity may have on the conduct or findings of the research. It is argued that the selection of a mixed method approach with the inclusion of qualitative methods implies the existence of a subjective approach (Hussey & Hussey, 1997), since qualitative data is subjective by nature since different people can perceive the truth differently. With this, the researcher’s experiences, beliefs, and values are incorporated into the research design and analysis of data, with qualitative researchers studying things in their natural settings, attempting to make sense of, or interpret, phenomena in terms of the meanings people bring to them. 5.1.3 Positivism or constructivism Positivism is based on a deductive, scientific process, looking for a cause and effect relation, drawn from an initial hypotheses, whereas constructivism is by nature more inductive, based on the interpretation of data to generate a conclusion, (Hussey and Hussey, 1997). Within the inductive approach theory is developed from the observation of empirical reality, and thus it is constructed. The inductive approach is thus similar to constructivism in so far as constructivism uses inductive reasoning. From a constructivist perspective knowledge is developed through the interaction with the natural world (Glasersfeld, 1990; Piaget, 1952; Piaget, 1969). Knowledge is thus not passively received but it is actively constructed through social
  • 102. 5. Research methodology and design 82 interaction and it has an important influence on the formation of language, thought, and finally of personality. (Vygotsky 1978). In accordance with Piaget (1952) knowledge is not a representation of the real world, but instead a collection of conceptual structures that results from the development of human intellect and proceeds through adaptation and organization. The existing knowledge of an individual is thus a result of past and existing experiences (Glasersfeld, 1989). This research further combines positivist and constructivist paradigms, as use of both paradigms was seen to be an appropriate means to provide the researcher with the ability to statistically analyse the data, whilst also allowing for an exploration of the complex set of variables that influence human behaviour. 5.1.4 Qualitative or quantitative Empirical research requires choosing whether to adopt a quantitative or qualitative approach, or some mix of the two. If in one way, quantitative research aims at generating statistics through the use of methods such as surveys or structure interviews, qualitative research aims at exploring attitudes, behaviour and experiences through such methods as interviews or focus groups (Dawson, 2002). A quantitative study, consistent with the quantitative paradigm, is an inquiry into a social or human problem, based on testing a theory composed of variables, measured with numbers, and analysed with statistical procedures, in order to determine whether the predictive generalizations of the theory hold true. In contrast, a qualitative study is an inquiry process of understanding social or human problem, based on building a complex, holistic picture, formed with words, reporting detailed views of informants, and conducted in a natural setting (Cresswell, 2009). The purpose of qualitative research is to examine the patterns of meaning which emerge from the data and these are often presented in the participants' own words. The task of the qualitative researcher is to find patterns within those words (and actions) and to present those patterns for others to inspect while at the same time staying as close to the construction of the world as the participants originally experienced it. Denzin and Lincoln (2002) point out that qualitative research is multi-method in focus, involving an interpretive, naturalistic approach to its subject matter. This means that qualitative researchers study things in their natural settings, attempting to make sense of or interpret phenomena in terms of the meanings people bring to them by the use of a variety of empirical materials. This constructivist notion that reality is changing whether the observer wishes it or not is an indication of multiple or possibly diverse
  • 103. 5. Research methodology and design 83 constructions of reality. Constructivism values multiple realities that people have in their minds. Therefore, to acquire valid and reliable multiple and diverse realities, multiple methods of searching or gathering data are in order and the use of investigators, method and data triangulations to record the construction of reality is appropriate (Creswell & Clark, 2007). In accordance to the literature, (Creswell and Clark, 2007; Morse, 2003), the use of quantitative and qualitative approaches in combination also provides a better understanding of research problems than either approach used alone. It can help answer questions that cannot be answered by quantitative or qualitative approaches alone, which was seen as relevant and to support the nature of this research. Quantitative methods appear to be in particular suitable to address a large population and thus produce results that are easy to code and standardize, (D. Morgan, 2007; Wilkinson & Birmingham, 2003). Such quantitative approaches are however limited to provide in-depth and detailed information and thus qualitative methodologies were subsequently used to explore the topic in more detail and to allow the voice, concerns and practices, of research participants to be heard, (Cole, 2006; Weaver and Olson, 2006). Using narratives and qualitative methods appeared to be however more adequate to better understand everyday energy practices, with structured questionnaires to gather a broader spectrum of data. As this research seeks to understand people and the social and cultural contexts within which they live, the qualitative approach of data gathering had thus been dominant throughout this study. Quantitative research in this study is therefore aimed to gain insight and identify issues for the subsequent qualitative phases of the empirical work, while the qualitative research aims to explore attitudes, behaviour and experiences through such methods as interviews or focus groups. The use of both, qualitative and quantitative methodologies allowed the researcher to embrace different aspects of energy related behaviours, as well as to address their diversity and complexity so as to better understand the meaning that people assign to energy use, exploring the full complexity of determinants that influence energy use, and to increase general understanding on how the adoption of more energy efficient behaviours could be promoted. The use of both groups of methods also supports the reliability, validity and quality of the findings, since both qualitative and quantitative researchers need to test and demonstrate that their studies are credible (Golafshani, 2003). With this the use of triangulation, a means of combining qualitative and quantitative research methods, could be seen as a viable approach to allow for
  • 104. 5. Research methodology and design 84 the “convergence among multiple and different sources of information to form themes or categories in a study” (Creswell & Miller, 2000, p. 126) and to reflect the multiple ways of establishing truth (Golafshani, 2003; Bergmann, 2011). Triangulation can be a means to overcome the influence the researcher has on the behaviour of participants, or in terms of the bias the researcher brings himself or herself into the conduct of the research (Easterby-Smith, Thorpe, & Lowe, 2002; Patton, 2002). Triangulation therefore allows for an increase in the reliability, quality and validity of the findings, (Bergman, 2011; Easterby-Smith et al., 2002; Golafshani, 2003; Patton, 2002). Triangulation in this context was thus also seen as a means to overcome the influence that the researcher has on the behaviour of participants, or in terms of the bias that the researcher brings into the conduct of the research. As Hussey & Hussey (1997) argued, the selection of a mixed method approach with the inclusion of qualitative methods implies the existence of a subjective approach, since qualitative data is subjective by nature as different people can perceive the truth differently. Further to this the research used some of the triangulation categories proposed by Stake (1995), namely data and methodological triangulation and multiple methods like surveys, focus groups and individual interviews, as well as theory triangulation during which more than one theoretical scheme in the interpretation of the phenomenon is used. As this research seeks to understand people and the social and cultural contexts within which they live, a mainly qualitative approach to data gathering was used. This research is designed based on a mixed, multi-method research approach, using both quantitative and qualitative research methods. As detailed by Cresswell & Clark (2007) and Morse (2003) the premise of using a mixed methods research approach is that the use of quantitative and qualitative approaches in combination provides a better understanding of research problems than either approach alone. As such a mixed methods research approach can help answering questions that cannot be answered by quantitative or qualitative approaches alone. 5.1.5 Available research instruments This research has been drawing on the following triangulation categories proposed by Stake (1995): data and methodological triangulation by the use of multiple methods (survey, focus group and individual interviews) as well as theory triangulation. In this exploratory study, qualitative and quantitative data collection techniques were used and the research methods applied throughout this work consist of
  • 105. 5. Research methodology and design 85 literature review, survey questionnaire, focus group interviews and in-depth individual interviews as depicted within Figures 5-1 and 5.4. Towards the beginning a range of potentially available methods was explored by drawing on available reviews of research methods, such as Creswell & Clark (2007) and Denzin & Lincoln (2002). Methods reviewed included: 5.1.5.1 Surveys and survey questionnaires Surveys, and more specifically survey questionnaires, are an instrument for collecting survey information, providing structured, often numerical data, that can be administered without the presence of the researcher (Cohen, Manion & Morrison, 2000:245). Surveys are often used to quantify or measure a concept. The goal may be to discover frequency of behaviour or to compare attitudes. Survey questionnaires are seen to be appropriate for those cases where the researcher intends to explore a topic by addressing a large number of people and to produce results that are easy to code and standardize, particularly if closed questions, with a limited set of possible responses (Wilkinson & Birmingham, 2003). Survey questionnaires are however limited in order to provide in-depth and detailed information and they have a limited scope of the data that be collected, and the limited flexibility of responses (Cohen, Manion & Morrison, 2000:245). 5.1.5.2 Thematic analysis Thematic analysis is highly inductive, with the themes emerging from the data and not being imposed upon it by the researcher, (Dawson, 2002). This type of analysis is highly inductive, that is, the themes emerge from the data and are not imposed upon it by the researcher. In this type of analysis, the data collection and analysis take place simultaneously. Even background reading can form part of the analysis process, especially if it can help to explain an emerging theme. Themes then form the overall structure for a content analysis that was carried out manually, using spread-sheets, (Litoselliti, 2003).
  • 106. 5. Research methodology and design 86 5.1.5.3 Content analysis Content analysis is commonly used by researchers in social sciences to analyse recorded transcripts and is based on the assumption that an analysis of language in use can reveal meanings, priorities and understandings, as well as ways of organising and seeing the world, (Wilkinson & Birmingham, 2003).” Often the message is delivered as a text, or converted to one (for example, an interview transcript may be produced or focus-group notes may be developed). In the conceptual analysis model, categories are developed and coded, and the number of occurrences of themes or issues is recorded. Content analysis thus could include the study and interpretation of written and visual material, for example, magazines, television advertisements, photographs. 5.1.5.4 Comparative analysis Comparative analysis uses data from different people that is compared and contrasted in a continuing process until the researcher is satisfied that no new issues are arising, (Dawson, 2002). Comparative and thematic analyses are often used in the same project, with the researcher moving backwards and forwards between transcripts, memos, notes and the research literature, (Dawson, 2002. 5.1.5.5 In-depth individual interviews Individual interviews are easier for the researcher to control than a focus group, in which participants may take the initiative, (Creswell & Clark, 2007). Individual interviews are a purposive sampling method, i.e. a sample based entirely on one's knowledge of the population and the objectives of the research, was selected as the most appropriate and in accordance with the literature, (Creswell & Clark, 2007, Powell, 1997). This is an understanding shared also by Leedy & Ormrod (2001) where people, or other units, are chosen for a particular purpose, implying the use of judgment by the researcher. 5.1.5.6 Telephone interviews Face-to-face interviews are the most expensive form of interview. The interviewer has to arrange a place to hold the interview and has to make the arrangements to get there and thus telephone interview requires far less resources, (Cassiani, Zanetti, & Pelá, 1992; Wilkinson & Birmingham, 2003). However, a major
  • 107. 5. Research methodology and design 87 limitation of telephone interviewing is its complexity and length of the interview since unlike the dynamics of face-to-face interviewing; it can be tiresome to keep the average person on the telephone for longer than 20–30 minutes and all of the body language data will be lost using this method (Lavrakas, 1993; Wilkinson & Birmingham, 2003). In addition to this, complicated questions, and in particular those that require the respondent to see or read something, are impossible via the telephone; so they are perhaps best used for short and very focused interviews (Wilkinson & Birmingham, 2003). The most common method to reduce resistance to participation has been to offer incentives (Tourangeau, 2004). 5.1.5.7 Grounded theory Grounded theory is a form of inquiry used in the areas of education and health research where the emphasis is on the generation of theory that is grounded in the data and that emerged from the data, (Dawson, 2002). This is different from other types of research that seek to test a hypothesis. In grounded theory, methods such as focus groups and interviews tend to be the preferred data collection method, along with a comprehensive literature review, which takes place throughout the data collection process so to help explaining the emerging results, (Dawson, 2002). In grounded theory the number of people to be interviewed is not specified at the beginning of the research as the researcher is open and responsive to where the research will lead and the research and data collection continues until a saturation point is reached at which no new information is being collected, (Dawson, 2002). • Ethnography as a phenomenological methodology using observed patterns of human activity The emphasis in ethnography is on describing and interpreting cultural behaviour and where the researchers immerse themselves in the lives and cultures that they study, including to live within the research population so to participate in their activities whilst observing the populations behaviour, taking notes, conducting interviews, analysing, reflecting and writing reports, (Dawson, 2002). Ethnographers highlight the importance of the written text because this is how they portray the culture they are studying, (Dawson, 2002).
  • 108. 5. Research methodology and design 88 5.1.5.8 Action research Action research is a systematic enquiry with the objective to obtain practical results that allow for improving a specific aspect of practice and to make those results available for further scrutiny and testing (Wright, 2008). Action research aims to deliver practical results that can be utilized to improve or correct a current state. Action research follows a four stages cycle (Figure 5-3) that emphasizes the importance of reflection on action (McMahon, 2007). Figure 5-3: Action Research Cycle (Wright, 2008). Action research is a deliberate and planned intent to solve a particular problem, or a set of problems, and by its nature involves strategic action, (McMahon, 2007 p.167). It is thus different to the reflective practitioner model as expressed, for example, in Kolb’s learning cycle as going through the cycle will not result in action research, (McMahon, 2007 p.167). Action Research draws on the interplay of dialogue and the involvement of a group of ‘stakeholders’ that are engaged in the process of inquiry and that collaboratively engage in a continuous cycle of analysis, reflection, planning and action, (Burns, 2006). In practice a challenge that action research faces is to establish a continuous inquiry circle, (Burns, 2006). 5.1.5.9 Focus groups Focus group research is a form of qualitative method used to gather rich, descriptive data in a small group format where participants have agreed to focus on a topic of mutual interest and where the emphasis is on understanding participant’s experiences, interests, attitudes, perspectives and assumptions (Wilkinson & Birmingham, 2003). Focus groups are an appropriate means to explore multiple perspectives of reality and how participants feel and think, (Cole, 2006; Morgan, 2007). They allow to explore individual beliefs and perceptions regarding motivation and barriers towards the adoption of more energy efficient behaviour at home and as such to gain insight into people’s shared understandings of everyday life, (Gibbs, 1997). They
  • 109. 5. Research methodology and design 89 draw upon respondents’ attitudes, feelings, beliefs, experiences and reactions; and explore the role that these individual beliefs, perceptions and social norms could be playing, (Gibbs, 1997; Mischler, 1986; Wilkinson & Birmingham, 2003). The purpose within the interview is not to elicit a multiplicity of views and emotional processes within a group context, but rather to explore on an individual basis the meaning and significance of what is happening, (Gibbs, 1997; Mischler, 1986; Wilkinson & Birmingham, 2003). Focus groups allow participants to share their specific experiences about the topic under investigation and with those experiences being explored in relation to predetermined research questions, (Merton and Kendall, 1987). They thus allow exploring the everyday use of language and culture of particular groups (Morgan, Krueger, & King, 1998; Powell & Single, 1996) so to produce data and insight that would be less accessible without the interaction found within a group, (Morgan, 1998). They allow for the interaction within the group based on topics that are supplied by the researcher, which for instance, group interviewing would have not allowed for, (D. Morgan, 1998, p. 12). This allows one to find out why certain topics are more salient than others, though on the downside there is less control over the data produced than in either quantitative studies or one-to-one interviews, (Morgan, 1998). Another possible downside of focus groups is that participants might not be expressing their own definitive individual view, but might be influenced by others in the group and/or the group dynamic, (Morgan, 1998). They are also not suitable to generalize findings due to the small numbers of people participating and the likelihood that participants will not reflect a representative sample, (Gibbs, 1997). 5.1.5.10 Direct participant observation Direct observation tends to be used in areas such as health and psychology and it involves the observation of a ‘subject’ in a certain situation, often using technology such as video, (Dawson, 2002). Direct observation is characterized by a prolonged period of intense social interaction between the researcher and the subjects, in the milieu of the latter, during which time data, in the form of field notes, are unobtrusively and systematically collected, (Bogdan, 1972:3). Given the nature of the research problem as outlined in Chapter 1, it was then decided to adopt a mixed method approach as being the most appropriate for this research project and as following further detailed. Each of the data collection methods used in this research project could be considered part of an overall
  • 110. 5. Research methodology and design 90 approach to improving the quality and validity of the research data and in accordance to the triangulation approach adopted. For the quantitative study a survey instrument had to be used as this was the methodology of choice for the Energyprofiler study with which this quantitative part of the research had been integrated. For the qualitative part of the study focus groups and in-depth interviewing were seen as the most adequate ways to provide evidence on how energy is used at home in the context of people’s everyday lives. In comparison to in-depth interviewing, focus groups appeared to have also an advantage when it comes to observing a large amount of interactions in a limited period of time. Despite the potential disadvantage of telephone interviews, the in-depth interviewing was made based on telephone interviews for logistical reasons and as existing research also suggest that telephone interviews are still suitable for short and very focused interviews (Wilkinson & Birmingham, 2003), which had been the case. Free translation was seen to be the most appropriate means, though it is acknowledged that potentially other methods could have been equally used, such as word-for-word, literal or semantic translation. 5.2 Methods used Through this research a preference has been given for inductive research, with the emphasis on an exploratory approach to improve the understanding of energy use at home and how the adoption of more energy efficient behaviour could be promoted. This research further combines positivist and constructivist paradigms, as use of both paradigms was seen to be an appropriate means to provide the researcher with the ability to statistically analyse the data, whilst also allowing for an exploration of the complex set of variables that influence human behaviour. As a result of blending such different approaches, this research applies a mixed, multi-method research methodology, using both quantitative and qualitative research procedures. As this research seeks to understand people and the social and cultural contexts within which they live, the qualitative approach of data gathering had been dominant throughout this study. Quantitative research in this study is therefore aimed to gain insight and identify issues for the subsequent qualitative phases of the empirical work, while the qualitative research aims to explore attitudes, behaviour and experiences through such methods as interviews or focus groups.
  • 111. 5. Research methodology and design 91 Initial research was undertaken using secondary sources, such as published literature, discussions with other researchers, or general media sources, to explore the overall aim of the research. This provided the basis for drafting an initial set of research questions and to deduce from those a number of questions for inclusion within the energyprofiler study questionnaire, (see section 5.3.2. for details). The energyprofiler study was being carried out in Portugal at the time of this research and offered the researcher an opportunity to contribute several questions and to access the survey data. Inclusion of data from this survey was seen as appropriate to support the initial exploration of the topic under research and so to be able to address a large population and thus produce results that are easy to code and standardize, (Morgan, 2007; Wilkinson & Birmingham, 2003). Such quantitative approaches are however limited to provide in- depth and detailed information and thus qualitative methodologies were subsequently used to explore the topic in more detail and to allow the voice, concerns and practices, of research participants to be heard, (Cole, 2006; Weaver and Olson, 2006). As such, the initial insight from the survey produced an indication into the characteristics and determinants of energy usage at home, as well as the factors that influence such. The objective was to obtain a basic understanding of the subject area, so to identify on where to focus in more detail subsequently, to fill gaps in the information. Focus group work was followed by individual interviews, which were considered an appropriate means to explore multiple perspectives of reality and how participants feel and think, in accordance to the work of Cole (2006) and Morgan (2007). The initial focus groups, (see section 5.4 for details), allowed the researcher to explore individual beliefs and perceptions regarding motivation and barriers towards the adoption of more energy efficient behaviour at home and as such to gain insight into people’s shared understandings of everyday life, (Gibbs, 1997). One objective in this regard has been to draw upon respondents’ attitudes, feelings, beliefs, experiences and reactions; focus groups allow for this. Individual interviews, (see section 5.5 for details), were then used to explore the role that individual beliefs, perceptions and social norms could be playing in terms of energy use and energy saving on a day-to-day base. The purpose within the interview is not to elicit a multiplicity of views and emotional processes within a group context, but rather to explore on an individual basis the meaning and significance of what is happening, (Gibbs, 1997; Mischler, 1986; Wilkinson & Birmingham, 2003).
  • 112. 5. Research methodology and design 92 The use of triangulation, (Bergman, 2011; Easterby-Smith et al., 2002; Golafshani, 2003; Patton, 2002), is thus seen to embrace different aspects of energy related behaviours, as well as to address their diversity and complexity so as to better understand the meaning that people assign to energy use, exploring the full complexity of determinants that influence energy use, and to increase general understanding on how the adoption of more energy efficient behaviours could be promoted. Triangulation in this context was thus also seen as a means to overcome the influence that the researcher has on the behaviour of participants, or in terms of the bias that the researcher brings into the conduct of the research, (Hussey & Hussey, 1997). Further to this the research used some of the triangulation categories proposed by Stake (1995), namely data and methodological triangulation and multiple methods like surveys, focus groups and individual interviews, as well as theory triangulation during which more than one theoretical scheme in the interpretation of the phenomenon is used. Figure 5-4 provides an overview of the research; namely literature review, survey questionnaire, focus group and in-depth individual interviews, as further detailed in the following sections. Figure 5-4: Research design. At the beginning of the research, a systematic search of published work had been carried out so to gain an insight and understanding into the research problem, to set the background and context for the research, and to identify gaps in knowledge and variables to consider in developing the key research questions. With this, information was collected about: (1) the challenge of sustainable development and how it relates to household energy use; (2) the contribution of the fields of economics, psychology and sociology to understand human behaviour; (3) the factors influencing energy use, saving and conservation at home; and (4) the different alternatives to enable and promote individual behavioural change. The literature review also included key academic theories within the chosen area and at a later stage, it helped to make sense of
  • 113. 5. Research methodology and design 93 the results obtained during the different phases of the research by comparing the findings with the literature. Pre-defined keywords were used to search a variety of on-line available academic journals and databases. In addition to this, bibliographies of works were examined so to locate additional published material that could be of interest to the research. Official homepages of public and private research institutes were consulted as well as personal homepages and blogs from established researchers in the field. Finally, the outputs of national, European and USA research projects and newsletters were reviewed, such as the Sustainable Development Research Network, (SDRN), so as to include the latest research findings. The results of this literature review allowed for the refinement of the initial research questions, as well as forming the basis for the empirical part of this research, and for the research methodology that are presented in the following. 5.3 Survey questionnaire A survey questionnaire was used during the initial phase of the research to gain insight and identify issues for the subsequent qualitative phases of the empirical work. The objective in using this survey data was to explore key issues identified during the literature review and more generally, to explore attitudes and behaviours to energy use in the Portuguese context. The survey questionnaire was designed and as part of a wider study, the energyprofiler study, that was being carried out at the time of this project. The energyprofiler study was a collaborative Portuguese national funded research project coordinated by the author of this research on behalf of Energaia, a local energy agency in Vila Nova de Gaia, Portugal, together with two additional project partners, Factor Social and Terrasystemics. A number of questions that were of equal importance to the energyprofiler study and the PhD research study were included in the survey. The researcher was allowed to reword some of the initial energyprofiler questions, as well as to introduce a set of further questions into the survey, so as to explore issues that were identified during the initial literature review. These questions were concerned with the visibility/invisibility of energy related behaviours, the role of individual beliefs, motivations and perceptions with regards to energy use, and on saving and conservation aspects, (as detailed in section 5.3.2). The energyprofiler study was the first national survey conducted in Portugal that collected data regarding individual perceptions, attitudes, competence and
  • 114. 5. Research methodology and design 94 patterns of energy consumption in the residential sector. With this the study attempted to identify and characterize the different segments within the Portuguese population, based on socio-psychological and demographic factors, so to support the development of policies, programmes and interventions with regards to energy efficiency at an household level, (Energyprofiler, 2011). 5.3.1 Survey questionnaire and data analysis methodology The energyprofiler study was based on telephone interviews with 1,019 Portuguese inhabitants, (aged 18+), that had been carried out between January and February 2010. The questionnaire was designed by the project team with the support of an external advisor, Professor Brenda Boardman (UK), drawing on a number of questions from previous surveys and it was refined through pre-testing before execution. The representativeness of the data was controlled through sample design, fieldwork quotas and post-fieldwork weighting. Data was weighted for the following characteristics: age, gender, area and sub-area. Results included in this thesis are based on weighted data unless otherwise stated. The survey data was analysed by the energyprofiler project team using descriptive statistics and included comparisons of means, (using t-test, ANOVA) and proportions, (using chi-square, Fisher's exact test, Binomial). This statistical analysis was used to characterize individuals regarding their perceptions, attitudes, competency, (cognitive and behavioural) and their associated energy use patterns. The results of these analyses provide the data used in this research. The energyprofiler survey questionnaire, (Appendix I), included the following four groups of questions: • Group 1; targeted at individual perceptions, attitudes and beliefs regarding climatic change, environmental problems, energy consumption and energy saving. • Group 2; targeted at energy consuming behaviour, existing level of information, competence and frequency of specific behaviours, motivations and barriers to action, as well as the usual sources of information regarding energy saving behaviour. • Group 3; targeted at household characteristics, such as the type of house, ownership, type of appliances in the house, as well as the amount of energy consumed.
  • 115. 5. Research methodology and design 95 • Group 4; targeted at the individual respondent, looking at characteristics such as age, gender, education and income.
  • 116. 5. Research methodology and design 96 5.3.2 Question added for the specific purpose of this research work For the purpose of this research three specific additional questions, (Q2, Q15 and Q6), were included in the energyprofiler questionnaire to provide an initial insight on two relevant concepts for this research: the visibility/invisibility of energy related behaviours and the role that individual beliefs, motivations and perceptions might play in terms of energy use, saving and conservation at home. The three questions that were included were: • Q2: “Which home appliances do you have at home that consume energy, (think about gas and electricity)?” This question related to the research question RQ1. • Q15: “Which reason(s) do you consider to be important to saving energy, (gas and electricity)?” This question related to the research question RQ2. • Q16: “Why don’t you try to save energy more often?” This question related to the research question RQ2. Q2 was included as an open format question where people were asked to provide a list of their home appliances that consumed energy. This question was expected to provide some insight into those appliances that people are aware of and also it might have been an indicator for the energy invisibility of certain types or groups of appliances, as well as for energy related practices. Q15 and Q16 aimed to provide an insight on individual beliefs with regards to, (a), individual motivations to save energy and (b), individually perceived barriers to saving energy. As for Q2, an open format was used. In addition to those three questions another seven questions, (Q8 to Q14), had been collaboratively formulated together with the energyprofiler project team and are detailed below. These questions were aimed to explore research questions RQ1 to RQ3 in a broader attempt to form the base for subsequent focus groups and individual interviews. The seven questions, (Q8 to Q14), are: • Q8 “Can you please order the following five behaviours from the one that saves the most energy, to the one that saves the least?”: the five behaviours were: 1. Reducing shower time from 15 to 10 minutes; 2. Turn off equipment, as opposed to leaving them on "stand-by" mode; 3. Replacing
  • 117. 5. Research methodology and design 97 incandescent lights by fluorescent lights; 4. Periodically defreeze freezer/fridge; 5. Wash at low temperatures (30-40 degree). • Q9 “When you turn the heating on in a room, what do you do with regards to the doors and windows?” with a list of four possible answers being provided. • Q10 “When is cold outside, what do you do to increase your comfort at home?” with a list of four possible answers being provided. • Q11 “Regarding the fridge and freezer, what do you do once you need to open it?” with a list of four possible answers being provided. • Q12 “Regarding the washing machine, what do you do when you need to use it?” with a list of four possible answers being provided. • Q13 “How do you turn off the TV and other appliances?” with a list of four possible answers was provided. • Q14 “Once you leave a room, what do you do with regard to the lighting?” with a list of four possible answers was provided. Q8 aimed to explore the existing level of knowledge regarding specific behaviours and to highlight any potential gap between the intent and impact of behaviour in terms of the energy use. The six questions, 9 to 14, relate to six specific energy related behaviours and to what people currently do when facing those specific situations. For each of the questions a defined set of answers was provided and respondents had to choose the behaviour that they could identify most with. The aim of these six questions was to assess the behaviours that are currently being performed and the frequency of their performance, so to assess the level of competence and performance to best practice. The energyprofiler study was thus important to contextualize the topic of the research, with the initial findings from the survey subsequently being further explored through the qualitative phase of this research work. The energyprofiler study also provided some understanding regarding the motivations to use and to save energy at home, as well as the main perceived barriers to change and provided some answers to what enables, explains or influences energy use and saving at home. The question on how to promote different behaviours, (RQ3), was not addressed with the energyprofiler survey. The energyprofiler study revealed
  • 118. 5. Research methodology and design 98 what seemed to be a gap between existing behaviours, motivations and barriers to saving energy, which was further explored during the subsequent phases of the empirical study. 5.4 Focus groups Focus groups, (FGs), were carried out with the aim of exploring in greater depth beliefs and perceptions regarding motivations and barriers towards the adoption of more energy efficient behaviours at home. This enabled the researcher to explore the more general process of energy related behaviour, without limiting the research to environmental questions, such as why individuals do not choose less environmentally damaging and less energy efficient behaviour. In this research, focus groups were used in a way similar to the work of Merton and Kendall (1987) by attempting to get participants to share their specific experiences about the topic under investigation and with those experiences being explored in relation to predetermined research questions. For the purpose of this research, focus groups were used to gather insights into, energy use, home energy saving and conservation, to explore motivations, attitudes and behaviours, as well as to prepare the ground for subsequently conducted interviews. The purpose was to explore the everyday use of language and culture of particular groups as suggested by Morgan, Krueger, & King (1998) or Powell & Single (1996). Instead of focus groups other research methods could have been used, such as direct participant observation, group interviewing, or in-depth interviewing, as a way to provide evidence on how energy is used at home in the context of people’s everyday lives. However in comparison to direct participants’ observation and in-depth interviewing, focus groups appeared to have an advantage when it comes to observing a large amount of interactions in a limited period of time. Since the FG methodology uses group interaction to produce data and insight that would be less accessible without the interaction found within a group, (Morgan, 1998). The focus groups did provide access to individuals' interaction on topics that would otherwise have been difficult to observe, such as informal group conversations regarding daily energy related behaviours, the determinants of actions and motivations to change. In line with the literature, the FGs allowed for, “The interaction within the group based on topics that are supplied by the researcher”, (Morgan, 1998, p. 12), which for instance, group interviewing would have not allowed for. The Interaction between participants allowed the researcher to understand their view of the world, the language they use
  • 119. 5. Research methodology and design 99 when discussing energy use, their values and beliefs, or the interaction with participants asking questions to each other so as to re-evaluate and reconsider their own understandings of their specific experiences. This allowed the researcher to find out why certain topics where more salient than others as the FGs simulate what in the literature is known as ‘a social gathering and interaction’, (Morgan, 1998) and which allowed for what seemed to be multiple interpretations that had been expressed by participants, with a number of explanations being provided as to their respective behaviours. Focus group methodology does nonetheless also have limitations. Firstly, there is less control over the data produced than in either quantitative studies or one-to-one interviews, since FG research is open ended and cannot be entirely predetermined, (Morgan, 1998). Secondly, because individuals might not be expressing their own definitive individual view, but might be influenced by others in the group and/or the group dynamic, (Morgan, 1998). Thirdly, the fact that focus groups are not suitable for generalizing findings to a population, due to the small numbers of people participating and the likelihood that participants will not reflect a representative sample, (Gibbs, 1997). Fourthly, the selection of group members will likely affect the outcome of the discussion itself, (Wilkinson & Birmingham, 2003). However, since the purpose of this research was to gain a particular insight into the topic and not to apply generalize findings to a population, FGs were still seen to be the most suitable research method. 5.4.1 Focus group objectives The objective of the focus groups was to explore a set of emerging findings from the energyprofiler study regarding the motivations to use and to save energy at home, as well as to identify the main perceived barriers to change, (RQ2). During the FGs the following themes were explored: • Perceived roles and functions of energy use at home • Self-perception of own energy use at home • Factors influencing energy use at home • Factors that could facilitate the adoption of more energy efficient or related behaviours FGs were structured with a predetermined list of open-ended questions and activities in order to elicit the constructions and perceptions of the participants and without imposing the researchers’ preconceptions.
  • 120. 5. Research methodology and design 100 Table 5-1 presents a free translation from Portuguese to English of the predetermined list of questions in relation to the objectives and techniques that were used. Table 5-1 – Focus group roadmap and techniques used. Question Objective Technique Q1.Think back to yesterday. What have you done that used energy? To list perceived energy consuming behaviours. Take people back + open question: write down on flipchart. Q2.When you think about energy what is the first thing that comes to your mind? To list first thoughts so to introduce discussion; expected results: identified daily practices. Open question. Q3.If energy was an object, what would be the individuals’ characteristics? Evaluate whether people can picture energy and to make it visible through the use of adjectives/characteristics. Follow up questions + metaphor and association; prompt colour, smell, 5 senses. Q4. If you would have the chance to save energy why would you do so? Identify motivations to save energy. Open question, followed by probing and prompting questions if required. Q5.Think back to any attempt you made to save energy. How would you describe the experience? Identify individual perceptions once saving energy, such as experiences, motivations or perceived barriers. Open question. Q5.1. What were the reasons for such a success/lack of success? Follow up question. Q6. Some people have been reporting difficulties to change their energy consuming behaviours. What is your personal experience? Open question and third party projection. Q7. We have been hearing that people say they already save/do all they can. How do you fell about it? Identify perceived barriers. Open question and third party projection. Q7.1. A number of reasons have been mentioned. I would like to ask you to write down the 3 most important ones one per post-it Follow-up question and group activity so to promote discussion for grouping those post-its and label the groups. Q7.2. How would you like to be helped to overcome such barriers? Follow-up question. Q8. Imagine you have been asked to develop a future intervention program to be launched nationwide. What would you include within it? Identify characteristic of interventions that were deemed to be desired. Role-play; prompting for mediums to use, type of message. Q9.Can you share an example you recall from any campaign promoting energy saving? Identify initiatives at the level of recognition and recall. Open question. Q9.1.Which components of the campaign have called your attention? Identify distinctive factors of campaigns, including characteristics that were deemed as being desired. Follow up question. Q9.2. In your opinion how useful do you find this type of campaign? Follow up question. Q10. Can you please draw an image for the campaign, or write the slogan you would use? To provide a summary of the discussion. Image and word association, drawings and slogans on paper base, group activity. Q10.1. What was the difference between this campaign and the ones you have just been mentioning? Follow up question. As can be seen from Table 5-1, a variety of techniques have been used to promote the discussion and interaction between FG participants, but also to reduce the influence of the researcher. To generate practical comparable discussions, a set of energy related behaviours were prompted during the FGs, such as
  • 121. 5. Research methodology and design 101 showering, lighting and cooking habits, but also room temperature and standby practices. These behaviours were determined by considering a number of factors, namely their impact on the energy bill, their likely visibility, their acceptability to the group, the feasibility of adopting the behaviour and the frequency the behaviour occurred. Within the FGs, the first set of questions explored those behaviours that were perceived as energy using ones, as well as the role and characteristics of daily energy use. Subsequently, participants were asked for motivations and barriers to saving energy at home and lastly they were asked for their input and perceptions about possible intervention programmes or communication campaigns to promote the adoption of more energy efficient behaviours at home. They were not specifically told that such programmes or campaigns must be appealing to them, but rather that it should be suitable for the population in general. This last part provided the researcher with an understanding of the kind of narratives, focus and messages that were perceived to hold a potential to promote behavioural change, to highlight potential gaps between motivations and barriers and to derive from this a possible roadmap for action. Though this research is focusing on day-to-day behaviours, discussion also included investment types of decisions, which provided an insight into how FGs’ participants understood the contribution to energy saving efforts of both groups of behaviours. 5.4.2 Focus group composition Results used within this research are the outcome of the seven FGs that took place between June and September 2011 in three different locations in North Portugal. In total 41 volunteers participated in the study and this sample is by no means representative, though, an attempt had been made to provide a heterogeneous mix of genders, age, education and income levels so to allow for a reasonable diversity of opinions and experiences to be revealed. Therefore participants were selectively chosen to assure the desired level of heterogeneity. Variable gender was chosen over age to promote a dialogue that could underpin specific gender energy consuming practices at home. Though any of these two variables could have been chosen, since findings from the energyprofiler study indicated that age, region and gender all seemed to influence the way individuals can be grouped in terms of energy use at home. Different
  • 122. 5. Research methodology and design 102 education and income levels had not been a variable for the FGs’ composition, though 4 of the FGs consisted of currently unemployed that were studying to obtain high school equivalent education, while the other 3 FGs consisted of participants in regular employment that held at least high school level education. When this research was initially designed, 4 FGs were planned: one with low behaviour, two with medium behaviour and one with high behaviours as the following Figure 5-5 shows. Figure 5-5: Initial focus group design. The initial assumption was that the participants for the four focus groups, (Figure 5-5), could be recruited from the group of over 900 people that answered the energyprofiler questionnaire and agreed to be contacted for follow-up activities. After contacting some of those respondents, it became nonetheless clear that such recruitment process would not be a viable option because of geographical distance and for the majority of cases the inability to drive long distances. Since the objective was to have face-to-face focus groups there was the need for a different FG format to overcome these barriers. Participants were instead recruited from the local population via two strategies. Firstly through invitation, (FG1, FG2 and FG3) and secondly by collaborating with a local training institute, from which two classes of adults that were enrolled in vocational training were recruited, (FG4, FG5, FG6 and FG7). As a result of this, a total of 7, (instead of the initially 4), FGs have been taking place, which still allowed for the desirable heterogeneity. In addition to this, this new approach allowed one dedicated FG that consisted of participants that work within the energy efficiency and renewable energy sector and as such to explore any notable differences in terms of behaviours, levels of knowledge, language, and motivations that could exist between expert and non-expert groups. Figure 5-6 presents the grouping of the 7 FGs. High behaviour Both genders Any age Medium behaviour Women Any age Low behaviour Both genders Any age Medium behaviour Men Any age
  • 123. 5. Research methodology and design 103 Figure 5-6: Partial and total distribution of focus group participants. At the beginning of the FGs, participants were invited to answer a simplified paper-based pre- questionnaire, which was a reduced version of the energyprofiler questionnaire, (see Appendix II). Based upon their responses participants were classified as, ‘low behaviour’ for those performing none or one energy saving behaviour, ‘medium behaviour’ for those performing between 2 or 3 energy saving behaviours, and ‘high behaviour’ for those performing more than 3 energy saving behaviours. Figure 5-6 shows the results of this questionnaire and highlights that the age group 25-45 might be overall overrepresented but also that almost half of the FGs’ participants report already performing more than 3 energy saving behaviours, (since they are classified as High frequency of behaviour (H)). Participants were not given a financial incentive to participate in their FG. H M L H M L <25 <25 25-45 5 25-45 >45 >45 <25 <25 25-45 1 1 25-45 2 1 2 >45 >45 H M L H M L <25 <25 25-45 4 25-45 >45 >45 1 <25 <25 25-45 25-45 1 1 1 >45 >45 1 1 H M L H M L <25 <25 25-45 1 25-45 >45 1 >45 <25 <25 1 25-45 25-45 1 3 2 >45 2 1 >45 H M L H M L <25 <25 0 0 0 0 25-45 1 25-45 9 2 0 11 >45 >45 1 1 0 2 <25 1 <25 1 1 0 2 25-45 2 3 25-45 7 9 5 21 >45 >45 2 2 1 5 20 15 6 41 Frequency of behaviour Male Female Frequency of behaviour Male Female FG7 Frequency of behaviour Male Female Total Frequency of behaviour Male Female FG5 Frequency of behaviour Male Female FG6 Frequency of behaviour Male Female FG3 Frequency of behaviour Male Female FG4 FG1 Frequency of behaviour Male Female FG2
  • 124. 5. Research methodology and design 104 5.5 In-depth individual interviews The information collected during the focus groups was subsequently used as the basis for six semi- structured in-depth interviews: three with focus group participants representing the energy consumers and three representing energy conservation providers. Interviews were semi-structured with a predetermined list of open questions so to guide the conversation and to allow the participants to express themselves without any restriction and without imposing on the researchers’ preconceptions. Individual interviews are easier for the researcher to control than a focus group, in which participants may take the initiative, (Creswell & Clark, 2007). Other qualitative methods that had been considered were direct observation or diaries. Direct observation tends to be used in areas such as health and psychology and it involves the observation of a ‘subject’ in a certain situation, often using technology such as video, (Dawson, 2002). For this research direct observation had been seen not to be suitable due to the difficulty of such methodologies once it comes to observing individual energy consuming behaviours at home and within the participants’ natural settings. Diaries are used as research instruments to collect detailed information about behaviour, events and other aspects of individuals' daily lives, with the narrative being built from the ‘actors’’ point of view, (Corti, 1993). Due to the number of energy related behaviours individuals perform on daily basis, diaries did however not seem to be a suitable method of research. 5.5.1 Interview objectives The in-depth individual interviews built on the findings of the FGs, namely the importance that individual beliefs, perceptions and social norms play in terms of energy use and energy saving on a day-to-day base. The objective of the interviews was thus to better understand the individual motivations and barriers towards the adoption of more energy efficient behaviours at home. In-depth interviews were used to explore the following topics: • To explore barriers to adopt more energy efficient behaviours from a consumer and a practitioner point of view. • To understand the meaning of ‘comfort’, ‘convenience’ and ‘normal’ and their perceived influence regarding energy use from a consumer and a practitioner point of view.
  • 125. 5. Research methodology and design 105 • To understand whether ‘comfort’, ‘convenience’ and ‘norms’ have been part of the considerations of practitioners when designing behavioural change interventions. • To explore different approaches that could integrate ‘comfort’, ‘convenience’ and ‘norms’ within behavioural change interventions in order to promote a reconsideration of these at home. To generate practically comparable discussions, a set of motivations, barriers to action and energy related behaviours sourced from the roundtable discussion of the focus groups were prompted during the interviews with energy consumers. Two different sets of questions were developed, (see Appendix III and IV,) one targeted at energy consumers and one targeted at energy intervention providers. Both groups were initially questioned about the overall degree of easiness or difficulty to save energy at home, as well as the reasons for such evaluation. Energy consumers were then asked for their understanding of ‘comfort’ level and ‘normal’ energy use at home, about the impact of energy saving behaviours and to identify potential energy saving behaviours that they would be willing to engage in. Energy intervention providers were asked for their understanding about what consumers perceived as level of ‘comfort’, ‘convenience’ and ‘normal’ energy use at home. They were also asked about their experience on behavioural change interventions and in particular for those interventions focusing on promoting the adoption of a different norms regarding energy use at home. Finally they were asked about possible intervention strategies that could be pursued in the future. 5.5.2 Sampling of interviewees A total of six interviews were performed, three with consumers and three with intervention providers. Considering the nature of the research, a purposive sampling method, i.e. a sample based entirely on one's knowledge of the population and the objectives of the research, was selected as the most appropriate and in accordance with the literature, (Creswell & Clark, 2007, Powell, 1997). This is an understanding shared also by Leedy & Ormrod (2001) where people, or other units, are chosen for a particular purpose, implying the use of judgment by the researcher. Consumers interviewees were selected from the participants of the FGs based on answers provided during discussion and notable with regards to ‘comfort’, ‘convenience’, ‘normal consumption’ and ‘norms’. These topics have been discussed to a greater extent within FG1, FG2 and FG3. Participants of the other four FGs were more concerned with saving energy as they could not
  • 126. 5. Research methodology and design 106 afford to pay higher energy bills and thus evaluated comfort as something that requires money. The three consumers interviewed were two men, (CID1 and CID2), and one woman, (CID3). Intervention providers were chosen as they had been involved in designing behavioural change interventions, or as they were involved in the policy making process of defining the priorities for national intervention. More precisely PID1 works in a department promoting energy efficiency at one of the Portuguese energy utility companies. PID2 works for the ADENE – Agência para a Energia, a Portuguese national energy agency, that is responsible for home energy certification, supporting the Portuguese government in the definition of policies and new legislation, but also managing a number of interventions promoting energy efficiency themselves. Finally, PID3 is a middle manager at ERSE- Entidade Reguladora dos Serviços Energéticos, the Portuguese energy service regulation body, responsible for managing a Portuguese national programme targeted at financing and sponsoring behavioural change intervention to promote energy saving, conservation and efficiency within the residential, services and industry sectors. 5.6 Summary of empirical study methods The previous sections discussed the main research methods that were adopted during the empirical part of this study and Table 5-2 provides an overview of the participants for each of the three activities as well as it clarifies the sample and process for selection of it. Table 5-2 – Summary of research activities. Survey Focus Group In-depth interviews Sample criteria The objective was to have a representative sample of Portuguese citizens from all regions, collected through quota sampling procedures, considering the aim of the study. The sample should be evenly distributed with regard to gender, age group, region and urban/rural area (see appendix X for detailed sample distribution). Participants were selectively chosen to assure the desired level of heterogeneity in terms of genders, age, education and income levels. A purposive sampling method, i.e. a sample based entirely on one's knowledge of the population and the objectives of the research, was selected.
  • 127. 5. Research methodology and design 107 Selection process Only one participant per household was considered for telephone interviews, performed by a recruitment and survey company - Consulmark (Gallup Group) nationwide. 1019 interviews were conducted in a total. Participants were recruited from the local population via two strategies. Firstly through invitation, (FG1, FG2 and FG3) and secondly by collaborating with a local training institute, from which two classes of adults that were enrolled in vocational training were recruited, (FG4, FG5, FG6 and FG7). A total of six interviews were performed, three with consumers and three with intervention providers. 5.7 Qualitative data analysis: Focus group and in-depth individual interviews Focus group and in-depth individual interviews were audio recorded and afterwards transcribed. In terms of primary qualitative data, a combination of thematic, comparative and content analysis was used. Thematic analysis was firstly used to search for keywords or concepts mentioned during the FGs and ID, and to identify overarching themes. Discussions of energy use could usually be found linked to words such as comfort, convenience, normal, and money or saving. Thematic analysis is highly inductive, with the themes emerging from the data and not being imposed upon it by the researcher, (Dawson, 2002). Drawing from Litoselliti (2003) themes then formed the overall structure for a content analysis that was carried out manually, using spread-sheets as the following example in Table 5-3 demonstrates:
  • 128. 5. Research methodology and design 108 Table 5-3 – Content analysis. Transcript extract Argumentative categories Overarching themes Male, FG3: we cannot separate energy use from economic development. 20 years ago once we were our kids’ age, our country was less developed, we were a poorer country. Our parents could not offer us what we today do to our kids… The appeal to consumption, with PlayStations, sound systems, a TV set in each room… once I was a child my parents had a single TV at home, and nowadays how many do we have? Change in consumption patterns; Change in the number of home appliances owned; Need to cater for a growing number of expectations and needs. Economic development as a factor influencing energy use at home; Number of owned appliances as a factor influencing energy use; Evolution of social norms as a factor influencing energy use. Content analysis is commonly used by researchers in social sciences to analyse recorded transcripts and is based on the assumption that an analysis of language in use can reveal meanings, priorities and understandings, as well as ways of organising and seeing the world, (Wilkinson & Birmingham, 2003). Comparative analysis uses data from different people that is compared and contrasted in a continuing process until the researcher is satisfied that no new issues are arising, (Dawson, 2002), and has been attempted within this research. Further to this, background reading was used as part of the analysis process, in particular to explain any emerging theme that was not considered in the initial literature review process. The results of the qualitative data analysis were then discussed as themes and subthemes and illustrative quotes are provided throughout this work. Both quantitative and qualitative data phases were conducted in the Portuguese language with findings and analysis translated into English by the researcher. Questionnaire roadmaps, analysis or illustrative quotes presented in this work were then translated, using a free translation style, focusing on the meaning in order to capture the idea and context of what was said. Other methods could have been used, such as word-for- word, literal or semantic translation, however free translation was seen to be the most appropriate means. 5.8 Research ethics For the purpose of this research, primary and secondary data were collected to explore how energy is used at home. The use of secondary data is identified and sources acknowledged. The target group for collecting primary data were citizens aged 18 and above, who have their main residence in Portugal. Permission to collect, transcribe and to use the data for the purpose of this research had been granted by the participants at the beginning of each of the quantitative and qualitative data gathering sessions.
  • 129. 5. Research methodology and design 109 In the case of the national survey questionnaire, respondents were chosen randomly through a professional company and they were informed about the purpose, methods and intended possible uses of the research as well as what their participation in the research entailed. FGs’ participants and ID interviewees participated voluntarily in the data gathering phases and no coercion was used at any time during the research. FGs’ participants and ID interviewees were informed about the purpose of the research, had the procedure explained that would follow and were given the option to leave the room if they wished. Neither EP respondents nor FGs’ participants and ID interviewees were given any type of compensation for participating in the study. Due to the methodologies used it is extremely unlikely there would be any direct harm to the research participants. No private and/or sensitive data was collected for the purpose of this research and as a consequence no ethical clearance was required from the OUUK. Once conducting the focus groups and interviews, commonly accepted techniques were used and special attention was paid to the design, revision and undertaking so to ensure integrity and quality. The confidentiality of information supplied by participants, and the anonymity of respondents, was respected and guaranteed due to the use of codes to represent FG participants and interviewees. Further, audio recordings and transcripts of the focus groups and interviews were kept confidential and in a secure location. No image that would allow visual identification was made during any of the phases of the empirical study. Collected primary data from the survey questionnaire was computed by the energyprofiler project team using SPSS, with the researcher being directly involved during the pre and post analysis of the data. This research uses the results of such analysis and no further analysis of data was performed. Qualitative data was analysed using commonly accepted analytical techniques, with a combination of thematic, comparative and content analysis used. 5.9 Summary This chapter explains the various options available during the field research part of this study and the logic for the selection of the specific approach, strategy and methods, some of which required a more subjective approach due to the nature of collecting, analysing and interpreting the more qualitative focus group and interview data. In summary the research is mainly of an inductive nature in terms of formulating a theory
  • 130. 5. Research methodology and design 110 from bottom-up, and using a multi-method approach that combines a survey, with focus groups and individual in-depth interviews as the primary research methods.
  • 131. 6. Exploring domestic energy use 111 6 Exploring domestic energy use Chapters 6, 7 and 8 present and discuss the findings from the empirical work as outlined in Chapter 5; namely from the energyprofiler survey questionnaire, ((EP), see 5.3), the Focus Groups, ((FG), see 5.4) and from in-depth individual interviews, ((ID), see 5.4). Individual interviews involved consumers, (CID), as well as intervention providers, (PID). The objective of using data from the EP was to set the broader context of the research, with the FGs and ID interviews exploring specific topics that emerged from the EP findings. The relationship between chapters 6, 7 and 8, and the research questions is shown subsequently in Table 6- 1. Table 6-1 – Relation in between chapter and research questions. Chapter RQs Chapter 6 RQ1: What explains energy use at home? Chapter 7 RQ2: What influences energy use at home? Chapter 8 RQ3: What is the potential role of intervention strategies on energy use at home? 6.1 Characteristics of domestic energy use The characteristics of energy use were explored in all stages of the research and two main characteristics emerged during the empirical study: the invisibility of energy in home and the fundamental role that it plays on day-to-day practices. 6.1.1 Invisibility as a distinctive characteristic of energy use During the FGs and ID interviews, energy was often reported as invisible, in particular referencing electricity. In fact, some of the FGs’ participants said that utilities such as water or gas were less abstract to them than electricity, as one FG participant summarized: “For instance with electricity I think it is more difficult because it's something one can't see. With a water tap open one can see the amount of water flowing”, Female, FG3
  • 132. 6. Exploring domestic energy use 112 A few FGs’ participants expressed this invisibility by comparing energy use with the purchase of goods and how less visible, intangible and more immaterial the purchase of energy can be: “Because energy, one does not buy in packages, (comparing it to the purchase of goods at a supermarket)”, Female, FG6 Given the overall agreement among FGs’ participants that energy and in particular, electricity, is something invisible and immaterial, the topic was not further prompted during the ID interviews. During CID, interviewees did not establish this relationship by themselves; whilst, contrary, it was brought up by PID interviewees, who frequently discussed how invisibility could increase the difficulty of promoting more energy efficient behaviours. This indicates a different level of awareness between consumers and intervention providers. On a day-to-day basis energy was reported as visible through a number of ways. During FGs, participants discussed their interaction with energy namely, (1), through the services and amenities energy provides for their home appliances, or, enrolling in practices, such as cooking, lighting, or washing for example; (2), when purchasing home appliances, as a moment in time where energy use was considered within the purchase process; (3), when paying energy bills, or buying bottled gas, or wood; this action reminded them of their energy use. As a starting point to exploring the question during the EP survey questionnaire, respondents were asked, in an open-format type of question without being prompted, to name all the energy-consuming appliances they owned at home. This question was aimed at understanding the respondent’s perception regarding those home appliances that consumed energy. An assumption in asking this question was that there would be a body of un-reported home appliances, as respondents either do not have those appliances, or because they do not recall having them as they did not associate such appliances with energy consumption, (i.e. insignificant or invisible energy consumption), (Energyprofiler, 2011). To exclude the possibility of non- existent equipment, the EP team compared the findings of the EP survey questionnaire with the penetration rate of such appliances within the Portuguese population, using the latest available data 13 . 13 "Household Expenditure Survey" (2005-2006 - INE)
  • 133. 6. Exploring domestic energy use 113 Figure 6-1 compares the difference between the numbers of home appliances EP respondents reported owning, (here presented in percentage) and National reported figures. Figure 6-1: Percentages of home appliances reported by EP respondents [n=1.014] in comparison to national ownership data, (Energyprofiler, 2011). Based on the findings illustrated in Figure 6-1, the EP team concluded that there appeared to be a gap between reported and owned home appliances, (Energyprofiler, 2011). EP findings indicate that respondents may have not reported some appliances and tend to underestimate, mainly, the smaller and technology/entertainment related appliances. The only exception to this is the cooker, which was the main underestimated large appliance. An explanation for this might be, that in Portugal cookers are frequently run on gas and not electricity, and that gas is, perhaps, not understood as being an energy source. With regards to underestimating small and technology/entertainment related appliances, one interpretation for this is that EP respondents have those appliances at home, but forgot to report them, due to their perceived insignificant energy consumption. From the data presented in Figure 6-1, this cannot be clearly concluded, therefore this matter was further explored during FGs by asking participants to report how they used energy at home the previous day. This question provided an extensive list of answers as summarized in Figure 6-2.
  • 134. 6. Exploring domestic energy use 114 Figure 6-2: Reported home appliances and practices during FGs once participants were asked what they did the day before. As can be seen in Figure 6-2, the list of reported home appliances and practices is extensive and comprehensive, and do not support the assumption that EP respondents might have forgotten to report home appliances based on low energy consumption. From the findings of the FGs’ participants it is not possible to conclude for or against any predominant reason. However, FG interactions seemed to have facilitated a recalling of a more comprehensive list of home appliances, as well as the respective practices. This suggests that during the EP survey, respondents might have simply forgotten to recall some of the home appliances that they owned. One such reason for forgetting home appliances could be simply not having recent interaction with the appliance or associated practices, and as the following quote indicates: “Usually I will use the washing machine each second day”, Female FG6 A further reason for not reporting appliances and practices has been an, apparent, underreporting of those which people do not need to interact with in terms of ‘switching on or off’: “W1: we are talking about the lights but there are other things that are always on like the fridge. W2: yes, I was excluding those things”, FG2 It could further be observed, that the moment of purchase served as a reminder to a few of the FGs’ participants and CID interviewees as to how much energy they use at home. Thus, it could be seen as a moment in time when energy appears to have a higher visibility, through product energy labelling for Practices Lights Entertainment appliances Lighting TV Stove Doing the laundry PC Fridge Doing the dishes Microwave Freezer Cooking Iron Radio Prepare some toasts Microwave watch Light and engine of the aquarium Listening to music Standby lights Water engine Ironing Washing machine Electrical gates Charge mobile Hoover Drill Charge camera Exhaust fan Playstation Watching TV Tumble dryer Gas for shower Charge tooth brush Presence light for kids Coffee machine Showering Boiler Fan Television set Battery of mobile phone Hot water Hair dryer Heat pump to heat water Vacuum cleaner Coffee machine Small appliances Hand-blender All other appliances that are on 24h Home appliances
  • 135. 6. Exploring domestic energy use 115 example, with narratives during the discussions suggesting a period of reflection before the purchase of such appliances. Overall, FGs’ participants reported considering different alternatives when buying home appliances, as well as being more aware of energy efficient items; but, that those might not be the final purchase, as the following quote summarizes: “I think we don't pay much attention to A-class appliances which allow you to use less energy. However, once we are looking for buying an home appliances there is a big difference in price”, Female, FG6 The quote above, also highlights that the purchase decision process embraces not only the amount of energy the appliance will use but also the investment required in buying more energy efficient ones, a phenomenon that research to date has identified as a barrier to the purchase of more energy efficient appliances, as well as the adoption of renewable energy sources, (Barenergy, 2011; Gardner & Stern, 2002, 2008; Jackson, 2005). From the findings of the FGs and the ID interviews, it was not possible to understand whether purchasing more energy efficient home appliances accounted for the majority, or not, of the purchasing decisions, but that the purchase itself might indeed provide energy with some visibility. In addition to this, energy bills were considered by the majority of FGs’ participants and CID interviewees as a moment in time when energy appears to gain some visibility. It remained, however, unclear as to how far energy bills actually contributed to energy visibility. FGs’ participants prevalent feelings was that energy bills provided little helpful information, in terms of the amount of energy being used, which suggests that energy bills in Portugal might be obscuring rather than helping understanding of their energy use. FGs’ participants provided a number of reasons for this: (1), energy bills are usually sent out bi-monthly and often report on estimated energy consumption, rather than real consumption levels; (2), Not all energy sources are accounted for through the energy bill. FGs’ participants seem to overlook energy sources that were not accounted for in the energy bill, such as bottled gas and firewood. FGs’ participants seemed to have difficulties in estimating their monthly use of bottled gas and firewood; (3), The fact that a significant number of FGs’ participants reported paying a fixed amount during 11 months of the year with the difference being paid in the 12 th month. Thus, this contributes to a lack of understanding of energy consumption on a monthly base, as the following quote illustrates:
  • 136. 6. Exploring domestic energy use 116 “I pay the same amount each month and only at the end of the year I pay the difference of the energy use. It's very difficult to know how much energy I used during the months” Male, FG3 The 12 th month energy bill was, apparently, a subject of close reflection for a significant number of FGs’ participants and CID interviewees; (4), Pay bills using direct debit, was reported to contribute towards the increased invisibility of energy use; (5), Portuguese energy bills also include surcharges, that are not related to energy use and that could account for up to 44.9 percent of the final price for electricity, (Eurostat, n.d.), that could hinder understanding how much energy is used. Some, but not all, of these surcharges are disclaimed within the bill, which contributes to a lack of transparency. Commonly, the above reasons question the efficacy of energy bills in the one form or another to provide an adequate level of information. 6.1.2 The fundamental role of domestic energy use The FG discussions and the CID interviews showed strong agreement in the fundamental role that energy plays for people, as the following quote summarizes: “Electricity allows us to use our five senses, by seeing TV, listening to music, (…), also the smell with a freshener, (…), to cook…,(not finishing to go through the remaining senses)” Female FG2 FGs’ participants and CID interviewees agreed that energy is fundamental to fulfil basic needs, such as cooking or bathing, but also aspects that belonged to normal needs and lifestyles and related to comfort, convenience or common practices. With this, some of the FGs’ participants also expressed some frustration that they could not fulfil all their needs without having to worry about the next energy bill, since energy was too costly to fulfil all their needs. As such there was an overall agreement among FGs’ participants and CID interviewees regarding energy as fundamental, vital or essential. 6.2 Determinants of domestic energy use Energy use at home is often explained as based on a set of factors and existing conditions, (EEA, 2013; Maréchal, 2010) and this section aims to explore such factors and conditions that had been reported during
  • 137. 6. Exploring domestic energy use 117 the empirical study and to reflect on determinants that are influencing home energy usage. The results for this section are given as a series of themes that emerged during the FGs and the ID interviews, as FGs’ participants and ID interviewees had not been directly asked for what determines their energy use at home. 6.2.1 Relation of behaviour and energy use Findings from the EP survey, FGs and CID interviews indicate that people have already adopted some more energy efficient behaviours. Q6 of the EP survey questionnaire, an open-ended question, asked respondents to explain what they were already doing to save energy at home. EP respondents were invited to provide a list of everything they did to save energy and as the resulting data is presented in terms of the frequency of answers in relation to the total amount of respondents. As Figure 6-3 shows, the responses provided by the EP survey included a range of efficiency and curtailment behaviours, (Appendix V provides a full list of answers). Figure 6-3: Reported energy efficient behaviours, in percent of total No. of respondents [n=1.014] (Energyprofiler, 2011). 0,0% 10,0% 20,0% 30,0% 40,0% 50,0% 60,0% 70,0% Bought a smaller fridge The thermostat is at a maximum of 18 ° Celsius Double glasses Insulation of the house I don’t use the pre-wash step in the dishwasher Have solar panels at home (thermal/photovoltaic) Insulation of doors and windows Energy efficient heating system Turn off the central heating during the summer Energy class A appliances Always use the washing machine/dishwasher completely full Cook with gas Hand wash the dishes Turn down the washing machine/dishwasher temperature Air dry the clothes Take a quick shower Others Use of efficient lamps Turn off appliances (and don’t leave them on stand-by) Turn off the lights when there is no one in the room 0,3% 0,4% 0,6% 0,7% 0,8% 1,2% 1,5% 1,7% 3,5% 8,2% 9,2% 10,3% 11,4% 11,6% 12,2% 13,8% 20,2% 34,4% 44,0% 61,7% Energy efficient behaviours
  • 138. 6. Exploring domestic energy use 118 The results, as presented in Figure 6-3, show that the most commonly adopted behaviours are curtailment behaviours of turning lights off and avoiding standby consumption. These curtailment behaviours are followed by the purchase of energy efficient light bulbs and home appliances, (energy class A appliances in Figure 6-3). In contrast to this, efficiency behaviours related to water and space heating were less reported. Figure 6-4: Frequency of reported energy saving behaviours in FG pre-questionnaire. Figure 6-4 shows the results of the FG pre-questionnaire, (see Appendix II for the full version of the pre- questionnaire) and as can be seen 34 out of 41 FGs’ participants reported to use energy efficient light bulbs, followed by 25 participants using A class or more energy efficient appliances, 17 participants controlling room temperature and 14 insulating their doors and windows. Equally, during the FG discussions and CID interviews, the purchase of energy efficient light bulbs and home appliances, as well as turning lights off and avoiding standby, had been reported as the most widespread efficiency and curtailment behaviours. These four behaviours could, during the discussion, be traced back to past nationwide interventions in which energy efficient light bulbs had been provided for free, or discounts offered for more energy efficient major home appliances. The four energy saving behaviours most often cited in the pre-questionnaire might,
  • 139. 6. Exploring domestic energy use 119 however, be the result of a bias, since they were already provided as options to answers for Question 2 in the same questionnaire. Since controlling room temperature and insulating doors and windows, had a high response rate in the pre-questionnaire, it only was discussed within the FGs once prompted. Thus, the reported behaviour appeared to not correspond to the actual, current, behaviour. However, the fact that the FGs took place during summer, when such behaviours are not performed, might have been an equally valid explanation and from observations this remains unclear. A second set of questions, (Q9 to Q14), in the EP survey questionnaire further explored the level of adoption of best practice, in terms of energy efficient behaviour, in six specific situations, as can be found in Table 6-2. Table 6 -2 – Reported energy efficient behaviours [n=1.014], (Energyprofiler, 2011). Specific Situation (by survey question) Reported results Question 9 – “When you turn on the heating system in a room, how do you leave the windows or doors?” 22.2 percent of respondents reported the adoption of best practice by answering that they not only close doors and windows, but additionally they insulated the house to prevent heat losses. Most respondents, (38.8 percent), closed doors and windows, without thermally insulating the house. Only about 4 percent of respondents did nothing, or only close windows/doors once they remember. Question 10 – “When it’s cold outside what do you do to enhance the comfort at home?” 42.8 percent of respondents reported the adoption of best practice by first putting on extra clothes and then increasing room temperature if necessary. Only about 5.6 percent of respondents seek high thermal comfort without worrying about energy conservation. A large percentage, represented mainly in "other" procedures, have no electric heating or fireplace and thus, don’t fit in this question. Question 11 – “What do you do once you open the fridge/freezer?” 65.5 percent of respondents reported the adoption of best practice by trying to close the door as quickly as possible and remove everything they need at once. Only about 5 percent of respondents did not indicate concerns about energy conservation related to fridge usage. Question 12 – “What do you do once using the washing machine?” 75.8 percent of respondents reported adoption of the best practice by always using the washing machine at maximum load and air drying their clothes. Only about 8 percent of respondents did not indicate concerns about energy conservation at this level. Question 13 – “How do you turn off the TV and other appliances?” 64 percent of respondents reported the adoption of best practice by turning appliances off. Still, a high percentage of respondents, (24.2 percent), reported using the stand-by option of the equipment. Only about 11 percent of respondents did not indicate concerns about energy conservation at this level, never shutting off or doing it once they remember. Question 14 – “When you leave a room what do you do in relation to the lights?” About 86.8 percent of respondents reported the adoption of best practice by reporting that, "As a rule, I turn off the lights when I leave a room". Only about 3 percent of respondents did not indicate concerns about energy conservation at this level, never turning off the light or only doing so once they remember. The responses shown in Table 6-2 indicate a good level of knowledge and adoption of more energy efficient behaviours regarding lighting and stand-by practices. Nevertheless, when it comes to other behaviours, such as interaction with major home appliances, home thermal insulation or showering practices, this level
  • 140. 6. Exploring domestic energy use 120 of reported knowledge and adoption of energy efficient behaviour, is less often reported which indicates it might also be less often adopted. From the above findings, in combination with the FG discussions and interview responses, the following could be learnt. Firstly, the energy efficiency of appliances does not, on its own, appear to necessarily be a guarantee of lower energy use, since it is the way that people use their appliances that influences actual energy consumption. This point will be discussed more in section 6.2.3 and is supported by literature, (Goldblatt, 2005; INE, I.P./DGEG, 2011; Lomas, 2010). The responses of FGs’ participants and CID interviews indicated that there, indeed, seemed to be a dissonance between the behaviour of purchasing an appliance in relation to its use. For example, a significant number of FGs’ participants reported buying energy efficient light bulbs, whilst at the same time paying less attention to the way they used the lamp, as exemplified within the following quote: “That's the reason why they developed the energy efficient light bulbs. They know we will not switch lights off”, Male, FG7 This suggests that, despite technological developments and the use of more energy efficient appliances, energy intense habits might still be maintained and therefore potential energy gains could be lost. This is described in literature as the, “Rebound effect”, (Khazzoom, 1980) and as illustrated in the quote, as a direct rebound effect. Findings further show that reported energy saving behaviour frequently focused on easy to perform behaviours that have no apparent impact in terms of comfort, convenience and wellbeing such as the one expressed in the quote above. These findings should, however, be evaluated with care for two reasons. Firstly, it was not always clear whether FGs’ participants and ID interviewees were influenced by what they perceived the researcher wanted to have as an answer, or, whether the responses are a consequence of participants wanting to maintain a consistency in their own reasoning, which from the literature is influenced by the, “Cognitive dissonance theory”, (Festinger, 1957). Secondly, energy seems to be strongly associated with electricity and seen as a synonym for electricity, or perhaps for electricity plus gas. Therefore responses might well be limited equally to such energy sources only.
  • 141. 6. Exploring domestic energy use 121 6.2.2 Building characteristics The majority of the FGs’ participants and ID interviewees seemed to understand the role building characteristics have with regards to the amount of energy used on a day to day basis, as well as the limitation that they represent to adopt energy efficient behaviour. Building characteristics discussed included age, orientation, size, building envelope, performance of installed heating/cooling system, as well as the potential to refurbish, or install renewable energy systems. Situations, such as not being able to reduce energy use due to lock-in effects, were reported by all 6 ID interviewees and by a few FGs’ participants, as the following quotes demonstrate: “There are already a number of technical solutions within building options that could protect the environment that, due to the fact of being so expensive, are not often used”, Male, FG3 “If we want to install a solar panel they are so expensive”, Female FG6 Two of the PID interviewees further considered building characteristics to be a strong determinant for domestic energy use and that other factors, such as location or style preferences, were of a higher, decision making, importance than energy efficiency when purchasing property. PID1 argued that only a small niche of the population seemed to take the energy efficiency of their new homes into consideration. Given that ownership of a house was not a segmentation criterion for selecting FGs’ participants and CID interviewees, it was not possible to understand whether the energy efficiency of new homes was a variable in the house selection process. 6.2.3 Growing number of home appliances A number of FGs’ participants and CID interviewees further acknowledged that they own a growing number of appliances in comparison to the past. By the past, they were usually referring to what their parents owned at that age, or when they were younger and still lived with their parents. However, no relationship was established by them between technological efficiency gains per appliance, the overall growing number of appliances, and the impact that this could have on the amount of energy being used. As a result of this and, apart from two cases, FGs’ participants and CID interviewees did not seem to be aware of the impact of the growing number of home appliances and related higher energy consumption. This phenomenon is
  • 142. 6. Exploring domestic energy use 122 discussed, within research, as one of the explanations for the, “Energy efficiency gap”, (Feenstra et al., 2009) and the PID interviewees supported this. Though not understanding the full scope of the increased number of appliances they owned, FGs’ participants provide a number of examples of this evolution of ownerships, such as increased numbers of TV sets per household, the change from washing clothes by hand towards a washing machine, or the growing penetration rate of heating/cooling systems. “I have an AC at my holiday house that I use to heat during winter and cool during summer. For sure afterwards I need to pay the bill, but it feels good. Maybe 15 years ago I didn't have an AC and I survived”, Female, FG2 The quote above not only shows that some of the FGs’ participants started to own home appliances they were not used to owning, but that this can also represent an evolution of needs and expectations, as a combination of comfort and affordance. Heating systems, both water and room, were also a part of the discussion among all 7 FGs. In general, FGs’ participants seemed to be aware of the impact that such home appliance can have in terms of contribution to electricity and/or gas bill. Nevertheless, in three FGs, one misconception was often observed in regard to the belief that one is saving energy by using wood, instead of gas or electricity. FGs’ participants seemed to believe they were saving energy without recognizing they were simply exchanging one energy source for another. Only one FG participant mentioned that the energy efficiency of their heating system had been a discussion point once building their house. 6.2.4 Energy efficient home appliances and overall energy prices Findings from the EP survey show that energy consumption was reported as the most important characteristic, (31.1 percent), when deciding to purchase electrical appliances. This is followed by energy labels 14 , with 29.2 percent. Lower percentages include the price/quality ratio, (17.8 percent), price, (16.8 percent), or power, (e.g. watts), (14.3 percent). However, those findings should be analysed with some 14 According to the European Union Energy Label Standard.
  • 143. 6. Exploring domestic energy use 123 caution since they are not in-line with other research in this area that shows a different order of purchasing factor priorities, with quality being first, followed by price and only then comes energy consumption, as presented within the results of the energyprofiler study, (Energyprofiler, 2011). One of the reasons for such a result might be that people were questioned about the main characteristics of their home appliances that they bought the year before, within a survey that related to energy use. This could have triggered energy consumption as the first answer. This apparent contradiction could also be observed within the responses of some of the FGs’ participants and ID interviewees: “I think we don't pay much attention to A-class appliances which allow you to use less energy. However, once we are deciding to buy an home appliances there is a big difference in price”, Female, FG6 The findings from the FGs and ID interviewees did not also provide any clear evidence on how relevant energy use can be when purchasing a home appliance. FGs’ participants and CID interviewees, however, identified higher purchasing prices as a barrier to the purchase of more energy efficient appliances, since this would require, – inter-alia – investing up-front with savings benefits only achievable in the medium- long term: “The price difference of A-class appliances is considerably more expensive which is a reason for not buying such class of appliances”, Female, FG6 During the FGs and the CID interviews, it was not possible to fully understand whether participants were, indeed, purchasing energy efficient home appliances, or whether their monetary situation presented a limitation to such purchases. Evidence was provided for both cases, both buying more energy efficient appliances and also for being unable to afford them, even though they were aware of the benefits: “I'm proud of having a heat pump at home since it was sold as being a very efficient solution to heat water…this makes me feeling happy with my decision”, Female, FG2 In order to fully understand the impact of the higher price of energy efficient appliances, in terms of energy use at home, requires understanding how the costs of running such an appliance could compare to the
  • 144. 6. Exploring domestic energy use 124 initial investment required. This is, in particular, meaningful since saving money had been reported as the main motivation to save energy at home, during the energyprofiler survey and one could expect that any change in energy prices, be it in absolute or relative, would influence consumption. However, this is not always the case and during the empirical work evidence was provided that challenged this assumption. During the FGs stage, two categories of participants were identified. Firstly a group that appeared to be able to afford higher energy bills and, secondly, a group that reported to have a limited amount of money to spend on energy. Participants belonging to the first group seemed to be aware of the need of saving energy and reported trying to do so. However, they also reported to be willing to spend a higher amount on energy, in order to maintain their desired level of comfort at home, which suggests that concepts of comfort and perceived needs might increase with income level. The second group included participants that reported reducing their energy use, to the minimum required, in order to fulfil what they perceived as basic needs, with some of those participants reporting that they could not afford services and amenities, such as room heating during winter, as they would have liked to. For this second group, using more energy was reported as not being a viable option because they simply could not afford it. This group of, what seemed to be, less affluent FGs’ participants might even be in an energy or fuel poverty situation as during the FGs, a significant number of participants from FG4, 5, 6 and 7 reported experiences that appear to be situations of energy and/or fuel poverty. Yet, there was an overall agreement among these less affluent FGs’ participants to aspire to lifestyles which lead to the adoption of more energy inefficient behaviours. Within this, they could be considered frugal consumers who are obliged to keep costs down. The discussions also showed a consensus among FGs’ participants that, if the price for energy was lower, or they could have more money to spend, (meaning the relative price of energy was reduced), this would result in them using more energy: “The reason for reporting to save is a monetary one, perhaps if they had more money they would use more energy”, (reporting on how she perceived others motivation to save energy), Female, FG4 “Depends on the individual financial circumstances: those spending more money on energy can afford doing so (…) they can pay more and save less”, Male, FG4
  • 145. 6. Exploring domestic energy use 125 These quotes indicate a possible relationship, not only between decreasing price and higher energy use, but also of increasing income levels and increasing energy use and that energy use would almost certainly increase if FGs’ participants either had more money to spend, or if energy prices decreased, making energy relatively cheaper. On the other side, if energy price did go up, this might not impact energy use that much in the short-term. Those, more frugal, FGs’ participants appeared to, perhaps, not manage to save energy as they already only use it for, perceived, basic needs. Some, more affluent FGs’ participants, in contrary appeared to not have such constraints. These findings provide further evidence, supporting the literature regarding energy use, as inelastic in the short term, but more elastic in the long term, as suggested by Sorrell (2007). This suggests that only at a certain price could one expect to see a reduction on energy use. Other, more affluent, FGs’ participants pointed out, however, that if they could afford to pay higher energy bills, they also would be doing so. This provides evidence supporting the body of literature that advocates that higher income might lead to higher energy use, (DECC, 2011; Gatersleben et al., 2002). These findings nevertheless raise a question regarding the effectiveness of those types of interventions targeted at changing energy prices. During the FGs, a number of such intervention types were discussed, such as taxes or subsidies, with subsidies being favoured by participants over taxes. Within five of the seven FGs a type of intervention was discussed that aimed at penalizing bad behaviours, (i.e. energy overuse), providing some further incentive for the good behaviour, (i.e. energy underuse). A significant number of FGs’ participants were receptive to the position of paying a penalty, which could be an increased energy price, compared to the standard price. Similarly, in those cases where energy was underused, FGs’ participants suggested a bonus for good performance. Nevertheless, the initial enthusiasm of FGs’ participants towards such type of intervention and the effectiveness of the intervention was not clearly established. In light of the discussion of the previous paragraph the validity of these responses is, perhaps, not entirely clear. 6.2.5 The evolution of cultural and social norms Institutional, social and cultural factors influence the way lives are lived based on the norms that are established. During the FGs and ID interviews, a common theme related to the evolution of standards of comfort, namely thermal comfort, or convenience of newly established practices, which were considered by
  • 146. 6. Exploring domestic energy use 126 FGs’ participants and ID interviewees to be a mix between individual preferences and social/cultural common understandings. FGs’ participants provided a number of examples for practices that have been evolving over time, as for instance heating or doing their laundry and dishes and how a new way of doing these has developed that was expected to be followed. This evolution seem to be the result of the interaction between the introduction of home appliances, the ability to operate them and what has become a normal way of doing these activities, as one of the FGs’ participants summarized it: “I don’t know how I could live without my washing machine. I know in older times people didn’t had one but nowadays…I mean I do know how to wash clothes by hand but just the idea of the cold water…”, Female, FG4 The quote expresses not only how people seemed to have adapted new practices at home, but also how these new ways might lock individuals into these new practices, creating a dependency on a day-to-day basis, with individuals finding it hard to change their domestic routines and behaviours. This is to say that the evolution in the number of appliances and associated practices seemed to be accompanied by an evolution of individual needs and aspirations that become normal: “We got used to the comfort, to have all lights, to see TV, we got used to all of this. That does not mean that if someone would take all of that away we would not survive.” Female, FG7 A question, therefore, was whether FGs’ participants and ID interviewees perceived these home appliances already as a basic need, or whether they were still considered as being a luxury. During the FGs and ID interviews, a number of participants and interviewees acknowledged that some home appliances and daily practices could be perceived as a luxury, based on the comfort level they were associated with. This was particularly evident when discussing shower practices and room temperature during winter. During the FGs, participants provided some examples of appliances that they considered to be fundamental for their day- to-day lives, namely the fridge, the washing machine, lights and the stove, due to the essential role that they play within daily routines. This dichotomy between basic and luxury need was explored in more detail during the CID interviews by asking interviewees if they were to reduce their energy use what would they consider as a basic need and what would they consider a luxury. CID interviewees experienced difficulty in clearly separating basic needs from luxury and it appeared that basic needs were understood as everything
  • 147. 6. Exploring domestic energy use 127 they currently do, meaning nothing would be considered a luxury for them. As such, basic needs included a reasonable room temperature, a reasonable amount of light and the required number of showers to feel clean. The definition of ‘reasonable’ has never been specified in detail, but rather remains as an abstract concept of having a brighter or warmer house. Luxury needs that hold a saving potential were reported in some areas, such as reducing shower duration, avoiding standby consumption, avoiding leaving on unnecessary lights and appliances, which could all be considered as avoiding energy waste. This suggests that, overall, FGs’ participants and CID interviewees appeared to be aware of what good practices are under specific situations. However, they did not perceive non-performance of good practice as being a luxury. Findings indicated, however, that knowing about good practice did not translate into concrete behaviour and, particularly, when comfort seemed to be a dominant need that is both socially aspired for and accepted. From the FGs and CID interviews no consistent narrative emerged of a moral obligation to use energy in a different way. 6.3 Concluding remarks This chapter discussed the findings from the empirical study that looked at how energy is used at home in terms of its characteristics and determinants within the Portuguese context. Table 6.3 provides an overview about the findings, how those relate to the research questions and any noteworthy observations, followed by a summary of the findings with regards on how they relate to the first research question, (RQ1) and the literature.
  • 148. 6. Exploring domestic energy use 128 Table 6-3 – Summary of findings relating to RQ1 Empirical study findings RQ Noteworthy further observation Chapter Section: 6.1. Characteristics of domestic energy use 6.1.1. Invisibility as a distinctive characteristic of energy use Energy appears to be generally seen as an abstract concept as a result of its invisibility. RQ1a Apparent gap between reported and owned home appliances, notably for the case of small and entertainment appliances. Energy being visible, (1), through the services and amenities it provides once using home appliances and developing practices, (2), once paying for energy bills and, (3), once purchasing home appliances, as this constitutes a moment of reflection where different alternative appliances are compared. RQ1a, RQ1c Scope of association between home appliance and associated practice and corresponding energy use remained unclear. Unclear understanding of the final purchasing decision: is it for or against energy efficient appliances? 6.1.2. Domestic energy use as being fundamental Energy to be seen as being essential for people to live the way they know and, in particular, to support what is seen as their normal lifestyle that not only fulfils the basic needs of water, food and shelter, but also perceived needs of comfort and convenience. RQ1c Energy is perceived as something rare and expensive, resulting in a need to save energy at home; in opposition with the preference to fulfil individual needs without any limitations, or concerns. RQ1c Findings indicate a strong association of energy to electricity than to any other energy source. A reason for this might be the fact that electricity is the main energy source for domestic energy use in Portugal.
  • 149. 6. Exploring domestic energy use 129 Empirical study findings RQ Noteworthy further observation Chapter Section: 6.2. Determinants of domestic energy use 6.2.1. Relation of behaviour and energy use The energy efficiency of appliances alone is not necessarily a guarantee of less energy being used, since the way people use their appliances equally influences actual consumption. RQ1b Focus on easy to do behaviours, with reduced impact in terms of comfort, convenience and wellbeing. RQ1b Turning lights off and avoiding standby consumption as the most often reported curtailment behaviours. Purchasing energy efficient light bulbs, as well as energy efficient home appliances, is reported as the most widespread efficiency behaviour. In contrary to this efficiency, behaviours related to water and space heating, were less often reported. 6.2.2. Building characteristics Individual choices are constrained and shaped by the socio-technical system, this is the homes they live in and the appliances they own. RQ1b 6.2.3.A growing number of home appliances Evidence of the growing number of energy using appliances to be found in the average home. RQ1b 6.2.4. Energy efficient home appliances and overall energy prices Despite the increased energy efficiency of homes and appliances, there has been an increase in domestic energy use, which could be, for example, a result of the way appliances are used as well as the rebound effect. RQ1b Unclear understanding of the importance that Portuguese people attribute to energy consumption of home appliances at the moment of purchase. Within the energyprofiler study energy consumption was considered to be the most important aspect, despite there had been equally contradicting findings within the same study, (Energyprofiler, 2011). Also through the subsequent FGs and CID interviews no clear evidence could be collected.
  • 150. 6. Exploring domestic energy use 130 Empirical study findings RQ Noteworthy further observation 6.2.4. Energy efficient home appliances and overall energy prices (cont.) Energy use as price inelastic in the short term but seen to be elastic in the long term. RQ1b, RQ1c Unclear relation between income level and energy use, through an observed tendency for higher reported income levels to be associated with higher reported energy use. RQ1b, RQ1c Evidence of energy and fuel poverty as a social and material problem. RQ1b, RQ1c 6.2.5. The evolution of cultural and social norms Needs developed over time, referring to basic requirements of water, food and shelter, as well as socially perceived needs of comfort, or convenience. All of these are perceived as belonging to a normal lifestyle, with evidence of comfort and convenience as socially framed needs or wants as custom within society. RQ1b, RQ1c Apparent social and cultural needs of owning more and more home appliances, behaving in a way that could be considered energy intensive and favouring the maintenance of comfort levels. A general tendency of understanding comfort and convenience as needs that must be fulfilled, but not as luxury needs. Being able to fulfil these needs appears to be socially and culturally accepted and almost desirable. Social and cultural factors influence the way lives are lived once practices have been established, with standards locking people into, what then, appear to be normal social practices. RQ1b, RQ1c For the Portuguese, house heating has a lower share of total energy consumption compared to European values, (70 percent on an average), which may be the result of milder climatic conditions, in combination with fuel poverty (Backhaus et al., 2012; BPIE, 2011). More affluent people appear to trade money for comfort and convenience, giving priority to individual and family wellbeing, rather than, for instance, environmental protection. Those in apparent energy and fuel poverty seemed to not be able to reach an aspired comfort level and in some cases they might even live in unhealthy conditions. RQ1b, RQ1c Most energy, in Portugal, is spent on house heating, in the kitchen and on water, though less evidence exists for Portugal, regarding the way people consume energy in their homes, as well as behaviours which hold the highest energy saving potential.
  • 151. 6. Exploring domestic energy use 131 Empirical study findings RQ Noteworthy further observation 6.2.5. The evolution of cultural and social norms (cont.) Behaviours appeared to be socially determined by norms, by what others around do and by copying the way that others around behave. This seemed to be, in particular, true once these behaviours had become routine. RQ1b, RQ1c There is little evidence that norms could help promoting more energy efficient behaviours. RQ1b, RQ1c
  • 152. 6. Exploring domestic energy use in Portugal 132 The following summary provides evidence on how the findings reported in this chapter provide answers to the research questions 1, (RQ1), what explains energy use at home and the sub-questions, (RQ1a), what are the characteristics of energy use at home, (RQ1b), what are determinants of energy use at home and (RQ1c), how do individuals understand their energy use. With regards to RQ1a and the characteristics of energy use at home, two characteristics emerged. First, the invisibility of energy has been perceived as a distinctive characteristic of energy use. Findings provide further evidence that energy is perceived as something invisible that, compared to other utilities, is intangible and abstract. Improving energy visibility was seen as a means to promote and foster the adoption of more energy efficient behaviours, though FGs’ participants and CID interviewees equally showed that even once visible, they had little knowledge about how much energy they use, both of which are well known from literature, (Brandon and Lewis, 1999; Darby, 2006; Goldblatt, 2005; Martiskainen, 2007). A well discussed example, the energy bill, showed that despite making energy visible the impact is limited and the empirical study seems to confirm the findings of Darby (2006) and Brandon and Lewis (1999). FGs’ participants prevalent feeling was that energy bills provided little helpful information, in terms of the amount of energy being used at home, which suggests that energy bills might obscure, rather than help, understanding of energy use. Their efficacy to provide an adequate level of information, that could support a comprehensive evaluation of energy use at home, was also questioned, as highlight by Darby (2006) and Brandon and Lewis (1999). In addition to this, from the findings of FGs and the ID interviews, it was not possible to clearly understand whether when reporting on energy use, FGs’ participants and ID interviewees only talked about electricity, or if they also referred to other energy sources, such as gas or firewood. Such a difference might be, however, of particular importance since findings have equally shown that energy as a concept holds a stronger association to electricity, than to any other type of energy source. Therefore, it might be assumed that participants might have understood energy as being synonymous with electricity. The second emerging characteristic of energy, (RQ1a), relates to the fundamental role energy plays in day to day life, a characteristic that was not challenged during the FGs and the CID interviews and which, indeed, is very much in line with the literature, (Geller et al., 2006; OECD, 2012; Sorrell, 2007). This characteristic, strongly related to the way individuals understand their energy use, (RQ1c), as this fundamental role appears to be mediated by the needs that it fulfils, including those that result from
  • 153. 6. Exploring domestic energy use in Portugal 133 existing lifestyles. Such needs in the majority related to comfort, convenience and wellbeing, practices that become habitual and thus perceived as being normal needs. This seems to match well with findings from literature and that suggests that concepts of comfort and perceived needs might increase with income level; an assumption supported by earlier research, (WWF, 2012; DECC, 2011; Gatersleben et al., 2002). Findings further show that reported energy saving behaviour frequently focused on easy to perform behaviours that have no apparent impact in terms of comfort, convenience and wellbeing. The strong dependency and reliance on energy might also explain why energy was perceived as expensive by FG and ID participants. This is to say that FGs’ participants and ID interviewees appeared to be quite comfortable with a certain level of normalization, where individual energy use is perceived and evaluated as normal, even though it was understood as being energy intensive. This observation supports findings from literature, (Bandura, 1977b, 1986; Cialdini et al., 1991; Cialdini et al., 1990; WWF, 2012) and only a few of the FGs’ participants challenged this normalization; but from the point of view of not being able to afford it, rather than not aspiring to such a lifestyle. Findings from FGs’ participants and ID interviewees further show that as long as it is affordable, they are willing to pay more for energy in order to maintain current lifestyles. This is to say the norm is rather towards the fulfilment of own needs and family wellbeing, and less toward environmental protection, (DECC, 2011), (RQ2). As a result of this reported normalization, little evidence could be seen that would suggest that norms could be used to promote more energy efficient behaviours, (RQ3), though they did appear to be determinants for energy use, (RQ1b) and consequently, a change in norms could reduce energy use. Other strong determinants that could be seen related to building characteristics, as these influence, to a greater degree, the amount and way energy is used at home, which aligns well with the literature, (BPIE, 2011; DGGE/IP-3E, 2004; Goldblatt, 2005). Nevertheless, only a few FGs’ participants understood, or have been aware, about the locked-in effect that this situation encompasses and that this too is well known from literature, (Goldblatt, 2005; Maréchal, 2010; Shove 2004). Energy prices were reported as influencing energy use, but not that often and provided further evidence in support of the literature, (DECC, 2011; Gatersleben et al., 2002, Sorell, 2007), regarding energy use as price inelastic in the short term, but more elastic in the long term. Nevertheless, this reduced level of energy use would, in accordance to those relevant FGs’ participants, change if they could afford to pay higher energy
  • 154. 6. Exploring domestic energy use in Portugal 134 bills, providing evidence to support literature that advocates higher incomes might lead to higher energy use, (DECC, 2011; Gatersleben et al., 2002). Findings from the FGs and ID interviewees did thus show a positive relation between energy prices and energy use, as well as between disposable income and energy use. This positive relation mirrors earlier research, (DECC, 2011; Gatersleben et al., 2002); Sorrell, 2007) and has been, for example, explained by the concept of price elasticity and demand saturation, (Sorrell, 2007). A further finding relates to what is known from the literature as energy and/or fuel poverty, (Buzar, 2007a; Boardman, 2010; UK Government, 2013). During the FGs, a significant number of participants from FG4, 5, 6 and 7 reported experiences that appear to be situations of energy and/or fuel poverty, which is in line with the assumptions from literature that this would be the case within Mediterranean countries, (Healy, 2003; SEI, 2003; SILC, 2007; WHO, 2012).
  • 155. 7. Factors influencing energy use at home 135 7 Factors influencing energy use at home Chapter seven explores the relationships between motivations and barriers of energy use in the home. The chapter discusses the findings from the energyprofiler survey questionnaire (EP), the focus groups (FG) and the in-depth individual interviews (ID) regarding what influences energy use at home (RQ2). 7.1 Motivational variables and energy efficient behaviours Motivations were explored initially during the energyprofiler (EP) survey, with Q15, an open-format question, (Appendix VI for full list of answers) and then further explored during the FGs and ID, to, in particular, better understand the influence that environmental concerns could have in terms of adopting more energy efficient behaviours. 7.1.1 The motivation for saving money Findings from the EP survey show that 7 out of 8 respondents, (n = 1.014), reported cost-savings as the most important motivation to saving energy. During the FGs and CIDs, to save money was put forward as the main reason for saving energy, thus reassuring the earlier EP findings. Moreover, the motivation to save, for monetary reasons, seemed to be even more important to those FGs’ participants with an, apparent, lower level of disposable income. For this group of less affluent FGs’ participants, energy costs seemed to have a higher impact on their disposable income, with participants reporting that it would be unfeasible to accommodate additional costs. Equally for FG1, the group that consisted of participants that work within the energy area and that are well aware of the environmental impact of energy use, monetary motivations to save energy were reported to be the most important ones. While cost-savings had been reported as the most important motivation, it could be equally observed that monetary motivation appeared to be in direct conflict with curtailment behaviours that would be required to actually realize such monetary gains. FGs’ participants and ID interviewees frequently pointed out the effort that would be required to engage in numerous energy saving actions that, in accordance to their view, only result in minor monetary savings for each of the actions undertaken. Engagement in a number of
  • 156. 7. Factors influencing energy use at home 136 actions on a daily basis and the requirement to reinforce the need of such actions to all family members was seen as inconvenient and demanding, as illustrated within the following quotes. “I try to do so, (switch lights off), but it's not easy. Sometimes I simply forget it. It's normal”, Male FG6 “I sometimes announce at home: one of these days I will burn a CD to play over and over, telling things as switch the lights off… switch this off…(talking about the need to recall family members what they should do)”, Female FG6 “I usually go around and switch lights off and indeed I get psychologically more tired of doing so than the energy I will save at the end of the month”, Male FG3 As can be seen from the quotes to engage in repetitive actions requires a constant effort, and thus while cost-savings might be the most important motivation to save energy, in practice this might not lead to actual savings. During the FGs and CIDs, it could also be observed that a focus on monetary motivation might even result in an increased energy use, for example by leaving low energy lights on, which in literature is referred to as the rebound effect, (Khazzoom, 1980, Sorrell, 2007, Gottron, 2001). Evidence from the FGs and CIDs suggest the existence of both, a direct and an indirect rebound effect. A direct rebound effect appeared to exists as some of the FGs’ participants reported using more of the resource, instead of realizing the energy cost savings, for example, by leaving energy efficient light bulbs on since they consumed less, or having longer showers, as they were able to buy bottled gas at a lower price. An indirect rebound effect appeared to exist, as some FGs’ participants reported that they would spend the money saved on things they could not have purchased otherwise. This is to say that a focus on financial saving appeared to indeed support potentially energy and carbon intensive behaviours, that then could reduce or, even cancel, the environmental benefit achieved through the energy saved. In addition to this, the focus on financial savings seemed to facilitate two misconceptions, namely that the use of off peak tariffs and wood are ways to save energy. These are misconceptions, since in both of such
  • 157. 7. Factors influencing energy use at home 137 cases energy is not being saved; with off peak tariffs people consume the same amount of energy, only pay less for it and by using wood instead of gas or electricity, people might not be saving, but rather substituting their energy source. “One thinks there is an associated cost and that one needs to save. This is the reason why I think about off peak tariffs and try to use them as much as possible” Female, FG2 For these two cases, the focus on cost-savings could have easily lead to a re-bound effect, as already discussed in 2.3.6 and 6.3. 7.1.2 Pro-environmental behaviour and pro-social motivations Pro-environmental and pro-social motivational variables that have been identified, mainly related to environmental concerns as well as the need for caring for future generations. Pro-environmental and pro- social motivational variables that could be observed related for example to social norms, or to personal, altruistic and moral motivations, such as environmental protection, or an individual feeling of doing the right thing. During the EP survey, the environmental motivational variable emerged as the second most important motivation to save energy after the monetary stimulus. More than half of the EP survey respondents reported environmental motivations as a reason for saving energy, with 1 in 3 reporting to focus on saving resources and 1 in 6 reporting a concerned with climate change. During the FGs, the majority of the FGs’ participants reported similar motivations towards the environment, though monetary motivation remained predominant, with the environmental component perceived as a secondary, side effect: “It's an additional saving to save on those, (environmental), resources”, Female FG6 Furthermore 1 in 6 respondents reported that they save energy for the benefit of future generations, a motivation that could also be observed throughout the FGs:
  • 158. 7. Factors influencing energy use at home 138 “There is the environmental motivation since our children are the ones bearing the consequences of our current habits.” Female, FG7 For both the EP survey and FGs, the concern for future generations seemed to be, however, comparatively low as an individual priority and notably so, when compared to the monetary variable. In 4 out of the 7 FGs, protecting the environment was put forward as being the right thing to do, the topic mainly came up in the context of recycling as part of pro-environmental behaviour when discussing effective ways to protect the environment. With this, FGs, and later CIDs, provided some evidence that saving energy could be seen as the right thing to do for environmental reasons, though the following presented evidence suggests that this actually might not be the case. The findings indicate that EP survey respondents and FGs’ participants hold very positive attitudes towards the environment, not only on a broader level, but also towards energy and resource saving. During the EP study eight composite scales were computed resulting from the aggregation of questionnaire items. Scales were psychometrically validated based on Cronbach Alfa/inter-item reliability analysis and Pearson’s correlation (for two item scales), which can be seen in the Table 7-1 below. Table 7-1 – Composite scales [n=1.014, F (2.89 , 2914.70) = 434.73, p = .000, η 2 =.57], (Energyprofiler, 2011).. Scale/Variable Items (see questionnaire in Appendix I) Reliability General attitude towards the environment Q1 (items 1-10, 12, 14, 17) α=.82 Knowledge on climate change and energy Q1 (items 3, 12, 13, 15, 16) α=.65 Perceived risk respond to climate change Q1 (items 2 e 4) α=.65 Frequency of environmental performance Q7 (items 1-7 + 10-12) α=.64 Attitude towards the conservation of energy and natural resources Q1 (items 1, 5, 6, 7, 9, 10, 14 e 17) α=.77 Knowledge in relation to energy conservation measures Q1 (items 13 e15) α=.70 Responsibility in energy use Q1 (items 11 e 18) α=.76 Attitude towards energy Q1 (items 1, 6, 9, 10, 14, 17) α=.72 Competence in the use of energy Q9-14 α=.52
  • 159. 7. Factors influencing energy use at home 139 In general, the scales had acceptable (α =. 60) to high (α =. 80) internal consistency levels and strong correlations (r above .50) suggesting the items have relatively high internal consistency and can be understood as a reliable measure of the variables they represent. Only the competency measure in relation to energy use has low levels of consistency. One reason for such could be the fact the individual items (Q9 to Q14) evaluate different aspects of energy consumption (heating, use of refrigerator, washing machine and TV lighting) and as such they might not be perceived as part of a single category. Figure 7-1, plots the average Likert scale values for the composite scales of, “General Environmental Attitude”, “General Environmental Knowledge”, “Risk Perceived of Climate Change” and “Environmental Behaviour”, contained within the EP survey. More information on the EP study and method are available in Appendix VII. Scale General Environmental Attitude General Environmental Knowledge Risk Perceived – Climate Change Environmental Behaviour Mean 4.22 3.76 4.29 3.44 S.D. 0.45 0.57 0.53 0.66 Figure 7-1: Average values for risk perception of climate change and attitude, knowledge and environmental behaviour [n=1.014, F (2.89 , 2914.70) = 434.73, p = .000, η 2 =.57], (Energyprofiler, 2011). As can be seen from Figure 7-1, EP respondents have a high positive assessment of the environment in general, suggesting a favourable opinion regarding environmental issues and their resolution. EP respondents show a high positive attitude, towards the conservation of natural resources and energy, which implies a favourable opinion in relation to energy conservation measures at home. Similarly, EP respondents reported having a strong responsibility towards energy use at home, revealing a high level of
  • 160. 7. Factors influencing energy use at home 140 importance in this action. From another perspective, and as shown in Figure 7-2, EP respondents reported and overall held, positive attitudes and knowledge for conserving energy at home. Scale Attitude (…) resources and energy Attitude towards energy conservation Knowledge regarding energy conservation Responsibility towards energy use Mean 4.24 4.23 3.64 4.23 S.D. 0.50 0.53 0.77 0.53 Figure 7-2: Values for attitude, knowledge and responsibility towards energy use [n=1.014; F (2.89 , 2914.70) = 434.73, p = .000, η 2 =.57], (Energyprofiler, 2011). The positive attitudes and apparent knowledge, as presented in Figures 7-1 and 7-2, did not seem to translate, however, into performance and frequency of pro-environmental behaviours. As can be seen from the same EP survey responses, (Q7), to separate waste, reuse bags, or control room temperature was reported as ranging from between, "Sometimes", to, "Often", depending on the specific behaviour, as Figure 7-3 illustrates.
  • 161. 7. Factors influencing energy use at home 141 Figure 7-3: Reported pro-environmental behaviours [n=1.014], (Energyprofiler, 2011). The frequency of reported behaviours, shown in Figure 7-3, was thus significantly inferior to the positive attitude shown in Figures 7-1 and 7-2, highlighting the potential inconsistency between global environmental attitudes and pro-environmental behaviours. This is to say that the favourable opinion of environmental protection presented in Figure 7-1, apparently did not translate into a high frequency of pro- environmental behaviours, indicating the existence of an attitude-behaviour gap. This does support earlier findings indicating that attitudes seem to have little predictive value for explaining behaviour, (Geller, 1981; McKenzie-Mohr & Smith, 1999) and thus, can lead to an attitude-behaviour gap, (Kollmuss & Agyeman, 2002). EP findings further show that some pro-environmental behaviours, such as re-using bags, or turning off the light when leaving a room, are more often reported than others, such as using rechargeable batteries, or turning off the standby mode of home appliances. During the FGs and the CID interviews the realtionship between positive environmental attitudes and actual behaviours, was further investigated to better understand the reasoning. Findings indicate that the positive attitudes towards energy saving seemed to be surpassed by the, individual, direct benefits of energy use, such as comfort and wellbeing, which were reported to rank higher on individual priorities as long as they remain affordable, (see 3.4.4.). This is to say that overall attitudes towards environmental and energy conservation, as demonstrated in Figures 7-1 and
  • 162. 7. Factors influencing energy use at home 142 7-2, might be high when evaluated in isolation, but when compared to other factors, they might be surpassed. In such cases there appeared a preference for comfort and wellbeing, over environmental and energy conservation. Thus in isolation, environmental and energy conservation might be strong motivational variables, but in conjunction with other variables, they might be comparatively weak. In such a situation, saving energy to save money or the environment enters into direct competition with the expectation and desire of maintaining established practices and fulfilment. This is well-known from the literature with suggested benefits and motivations, for example, being convenience and comfort, (Barenergy, 2011, Darnton, 2008, Darnton et al., 2011, Jackson, 2005, Prendergrast et al., 2008). A further observation of inter-dependent and inter-related factors concerns financial and pro- environmental variables, in conjunction with differing points in time. The majority of FGs’ participants, being more or less affluent, demonstrated concern with their current financial-economic situation, which was seen as a concrete, near term threat, compared to the potential consequences of their energy use in environmental terms which was perceived as a more abstract long-term threat. This was, for instance, expressed by a number of participants through their understanding that today’s generation would not suffer the consequences of predicted environmental problems. Only a few FGs’ participants, and only one CID interviewee, reported to be sceptical that they would not suffer at all from such negative consequences. Negative consequences, referred to the fact that today’s generation might already be suffering from scarcity of resources, such as petroleum or water, but not necessarily from the environmental impacts of their use. In the opposite direction, the financial economic crisis was described as something that FG participants and CID interviewees were currently experiencing and perhaps, even affected by and that, therefore, did concern them. FGs’ participants, CID and PID interviewees also acknowledged the difficulty in understanding the relation between individual energy use and the environmental damage, which together negatively influenced their individual motivation to save energy. Some FGs’ participants claimed to not be able to understand the value of the contribution of their individual energy consuming behaviours and thus they do not know whether their consumption could be classed as normal or not, as the following quote shows:
  • 163. 7. Factors influencing energy use at home 143 “What is a normal use? How much energy is it per day? And if I consume above that level, what happens? Do I need to use x more kilos of coal? Is that what it means? One cannot understand”, Female, FG2 With this, it appeared as if the inability of understanding the consequences of ones actions led to a sense of helplessness and disempowerment. This supports earlier findings from Thøgersen (2005), that reduced levels of knowledge, regarding the environmental impact of ones behaviour, including energy use, appears to influence the ability to act in accordance to individual positive environmental attitudes. Further to this, the majority of the FGs’ participants perceived the behaviours of others as having a more direct impact on the environment then their own energy saving behaviours. There was a strong consensus among FGs’ participants that they perceived saving energy as having a lower impact on the environment in comparison to other behaviours, such as water saving or recycling, though no underlying reasons could be perceived: “I don't think one thinks I will save energy in order to protect the environment, I will recycle to save the environment, that might work out”, Male FG7. Another motivational variable that had been examined was the limitedness of resources as a motivation to use less energy, which the majority of the FGs’ participants did not seem to take into account. All three CID interviewees, in contrary, reported to understand energy sources as something limited and one reported energy scarcity as a fundamental reason to reduce his energy use. In summary, the findings presented in this section indicate that environmental motivations appear to not play an important role in inspiring people to adopt more energy efficient behaviours for a number of reasons as has been discussed through this section, most notably because of an apparent lack of motivation. FGs’ responses have further shown the potential existence of an attitude-behaviour gap, thus support earlier findings provided by Kollmuss & Agyeman (2002). Such an attitude-behaviour gap might explain the, apparent, observed dissonance between very positive attitudes towards the environment and resulting actions. Once it comes to action, participants seemed to position environmental concerns at a lower priority level, compared to, for example, financial, or family comfort and wellbeing issues.
  • 164. 7. Factors influencing energy use at home 144 7.1.3 Needs and expectations and its relation to motivation for saving energy As can be seen in section 6.2.5, social norms have been found to be potentially strong determinants of energy use. From a motivational perspective, social norms, however, did not appear to be a strong determinant to save energy at home, though it was extensively recognised, once talking about barriers, as detailed in section 7.2. During the EP survey, only 3.6 percent were concerned with the social component for saving energy, or status, (2.6 percent), or self-image, (2.7 percent). Social norms were however reported during the FGs, the CID and PID interviews, to play an important role in pro-environmental behaviours, such as recycling and water conservation. As a motivational variable to save energy, social norms were however, reported to be overall of low importance. This is not surprising, as FGs, the CID and PID interviews equally did show that current usage levels are frequently understood as being normal, (see 6.2.5), and therefore, the social norm is determined by current energy use, which is expected to accommodate all needs and expectations. 7.2 Barriers for adopting more energy efficient behaviours Barriers were explored initially with Q16 of the energyprofiler survey, in an open-format question, (Appendix VIII for full list of answers), that asked respondents to provide their reason(s) for not trying to save energy more often at home. Findings indicate that EP respondents in the majority, believed they were already doing everything they could to save energy and a question for the FGs and the ID interviews, therefore, was to explore if this, indeed, has been the case, or whether there might be any barriers that lead to the conclusion of having done everything. The frequency of responses during the FGs (see Appendix IX for full responses), when asked to provide three reasons for not saving energy, are presented in Figure 7- 4, in the form of a word cloud, subsequently shown in grouped format in Figure 7-5.
  • 165. 7. Factors influencing energy use at home 145 Figure 7-4: Reasons for not saving energy at home – responses from FGs Figure 7-5: Frequency of category groups of barriers during FGs. As will be seen through this section, not all such initial reasons for not saving energy at home appeared to ultimately play a role, while others did. 7.2.1 External/macro barriers: policy based, structural and economic barriers As shown in Figure 7-5, economic conditions where put forward as potential barriers for adopting more energy efficient behaviours. FGs’ participants and ID interviewees put forward two economic barriers that, both could be classified as policy based barriers. Firstly, a few FGs’ participants felt that only those appliances that are considered by law as being energy efficient should be available for purchase. In their view, such compliance to minimum standards could, however, only be achieved through policy measures, as postulated in the literature, (Barenergy, 2011). Thus a lack of such measures could be seen as a barrier. Barrier Comfort Habits Willingness Laziness Resistance to change Self- indulgence Environment Future Initial investment Return on the investment Information Actions currently taken Economic conditions Social norm, social dilemma, hypocrisy Frequency 6 4 6 7 6 8 34 9 16 15
  • 166. 7. Factors influencing energy use at home 146 The second barrier discussed within five of the FGs, related to penalty and incentive mechanisms that could promote the adoption of more energy efficient behaviour at home. According to the FGs’ participants, penalty and incentive mechanisms could only be promoted through policy-making interventions and thus, the lack thereof again constituted a barrier to them. Two more, further, barriers could be observed during the FGs and the ID interviews, both of which appeared to belong to physical-structural barriers, namely housing and existing home appliances. The infrastructure of the house was seen as being a determinant of energy use at home. This barrier was particular discussed in CID and PID interviews and there was strong consensus regarding the importance of house infrastructure, as well as the difficulty of intervention, even when technical and economic options are available: “There are a set of solutions that can protect the environment, namely in terms of the way the house is build, that for the reason of being so expensive are not used”, Male FG3 “I have the limitation of living in an apartment building which does not allow me to take actions in an independent way in order to save energy”, CID2 “If we want to install a solar panel they are so expensive”, Female FG6 There was a strong consensus that changing existing infrastructure will not only be cost intensive, but also only feasible once existing home appliances are out of service, or when technological solutions become more economically viable. As such, the findings aligned well with the literature, (Gardner and Stern, 2008; Martiskainen, 2007, Goldblatt, 2005, Maréchal, 2010). For the case of efficiency behaviours, with which an initial investment is required, not being able to afford the purchase of more energy efficient appliances was often reported by FGs’ participants as an economic barrier towards the adoption of more energy efficient behaviour. This barrier was more predominant within FGs 4, 5, 6 and 7, which appeared to be less affluent, though it was also discussed with a slightly different focus with the remaining FGs. In the case of the less affluent FGs, the discussion focused more on the purchase of energy efficient home appliances, the more affluent concentrated on the need for improving the building itself, or install renewable energy solutions. This division resembles the discussion from section 2.4.4, 2.4.5 and 6.2.4, regarding the influence of
  • 167. 7. Factors influencing energy use at home 147 economics, energy prices and income levels in terms of energy use at home. With this all the FGs considered economic aspects and financial limitations as constituting barriers. For the former group, the barrier related to curtailment behaviours, while for the latter group, it related to efficiency behaviour, similar to the discussion in section 6.2. 7.2.2 Knowledge based barriers With regards to knowledge based barriers, the findings have been somehow contradictory, as the results indicated that participants had adequate information, yet they argued the existence of some types of knowledge barrier and thus, lack of information. That participants had adequate information could be seen, for example, from EP respondents who reported an average-high level of general environmental knowledge, as well as knowledge of measures for conserving energy at home. Furthermore, half of the EP respondents reported already doing everything they can and 1 in 5 reported their current actions as sufficient. A smaller percentage, (16.9 percent), of the EP respondents reported that they would like to do more, but did not know how. Similarly, lack of information has been the most often reported barrier for not saving more energy at home during FGs, as can be seen in Figure 7.5 (page 127) Equally similar to the EP responses, the wider findings of the FGs did indicate that participants actually appeared to have such knowledge. These, partly contradictory, findings are presented below. Both, FGs’ participants and ID interviewees, frequently expressed difficulty with regards to one of three aspects: (1), lack of information regarding their overall energy use, (2), lack of information regarding the contribution of specific home appliances and behaviours to the total amount of energy used and (3), as a result of the previous two reasons, a lack of information regarding the amount of energy that can be saved by adopting more energy efficient behaviours. Regarding the lack of knowledge, in terms of overall energy use, during the FGs, there was overall agreement towards the difficulty of understanding how much energy they used at home. This was even the case for participants of FG1 that work in the energy industry. This difficulty was perhaps less a result of not being able to understand ones energy use, but rather due to the lack of feedback systems that could provide meaningful real time information.
  • 168. 7. Factors influencing energy use at home 148 Men1: I have the understanding of saving when I switch the lights off that I’m saving something but I don’t know how much that is. Men2: But that’s it...you have the feeling...I substitute my TV against a more energy efficient one and I have no idea how much that could save me. I can’t know since I don’t have an energy meter...if I would have one I would now how much I save, FG1 Similarly EP responses on providing a monthly, or an annual, figure for respondents’ electricity and gas consumption, (Q29, Q30), showed a significant lack of knowledge on how much energy is used on a monthly and yearly base. Most EP respondents provided an average annual cost for electricity, of 126.93€, (SD= 133.81€) and of gas, 111.07€, (SD = 86.31€). For monthly values, electricity corresponds to 67.55€, (SD = 35.33€) and gas 56.27€, (SD = 35.94€). During the FGs, few participants reported how much they pay for energy and even CID interviewees, once asked directly, hesitated in providing a value. Once provided, the value appeared to be rather an estimated value. In addition to this, participants in four of the FGs and also CID interviewees reported their energy use, not in kW, but in Euros, thus indicating that the amount of energy used is not really known and focuses, very much, on the price. Nevertheless, this evaluation seemed to be strongly associated with monthly energy bills, (electricity and piped gas in Portugal), and less with other energy sources, such as bottled gas or firewood. As an apparent consequence, people neither knew how much energy they were using, nor did they seem to be able to refer to energy in any other variable than the monetary one. “There is no other way to measure energy use, one does not know, I personally don't know another way to measure apart from the amount I pay for energy” Female, FG4 Further, findings did show an apparent disadvantage to the current design of energy bills, which made it difficult to separate an increase in energy use from changes in the price, or of isolating its price from other surcharges that are included within energy bills in Portugal. In regard to this, most of the FGs’ participants did not understand how to interpret the amount of energy used; with regards to if it could be considered normal:
  • 169. 7. Factors influencing energy use at home 149 “The single indication I have that I use little energy is due to the amount I pay since I don't even know whether it's little or too much” Female, FG2 The majority of the FGs’ participants claimed to not understand what a normal energy use level at home would be. For most of the FGs, a detailed discussion on what normal means, usually took place at this point in terms of how to define normal, what should be included, or excluded, or how to accommodate specific individual and family circumstances. The majority of the FGs’ participants concluded that normal energy use would need to be calculated in relation to some sort of variable, such as persons per household. FGs’ participants showed a common agreement that knowing this normal value for the energy use at home, would allow them to compare their own energy use with others, in order to understand whether their energy use was above, below or normal. In terms of the contribution of specific home appliances and behaviours, the majority of FGs’ participants and CID interviewees revealed several doubts regarding the contribution of different home appliances and energy related practices: “I don't feel ready to reduce the energy I use. I don't know how much each appliance is using, each lamp and as a consequence I can't reduce the energy used” Female, FG4 “Last year I bought an electrical oven (…) and I was curious to see how much energy it used so I would do a roast or bake a cake and would check for how much energy it was using. And I learned that for a roast I needed 4, a cake 2 (referring to energy units), I already cannot remember but by that time I learned how much energy I was using” Female, FG7 “1st women: I think that we don't know things we could to do (to save energy) 2nd women: and other times we don't do because we do not want to pay attention to the information” Female, FG6 While the quotes above illustrate doubts regarding the contribution of different home appliances and energy related practices, they also illustrate an apparent unwillingness to engage and lack of interest in the subject. With regards to the perceived overall energy saving potential at home, only a quarter of EP
  • 170. 7. Factors influencing energy use at home 150 respondents answered the question, (Q31), regarding the potential for saving energy at home, reporting an average saving of 16.48 percent. One of the respondents reported the potential reduction in Euros, reaching an average of 18.05 Euros per month, which was less than the percentage cited. This again suggests some difficulty in evaluating and calculating energy saving potentials. This difficulty of understanding energy use and the saving potential of specific behaviours was further demonstrated once EP respondents were asked to list five energy saving behaviours, from the one that saves most energy to the one that saves the least, (Q8). The list of the five energy saving behaviours included the following: (1), “Use the washing machine and/or dishwasher at low temperature (30-40º)”; (2), “Defrost periodically the fridge/freezer”; (3), “Replace incandescent light bulbs by fluorescent ones”;(4), “Turn off an appliance instead of leave it in stand-by”; and (5), “Reduce the shower time from 15 to 10 minutes”. EP survey results show that the ordering is not aligned with the actual impact of the five behaviours computed by the energyprofiler project team. According to the project teams’ calculations, the individual behaviour with the highest potential for saving energy would be to reduce shower time, followed by eliminating all stand-by consumptions. EP respondents considered those two options however to be of a lower impact, with only 17.76 percent considering a reduced shower time and 12.95 percent considering eliminating all stand-by consumptions as having a high impact. Instead, “Replacing incandescent light bulbs with fluorescent ones”, had the highest percentage, (77.53 percent), followed by ”Using the washing machines in programs for low temperatures”, (70.65 percent). This suggests that EP respondents might lack knowledge regarding the impact of specific energy saving behaviours. However, this finding should be evaluated carefully, since not being able to order a pre-given number of behaviours, does not automatically imply that EP respondents, in general, possess limited knowledge of the subject domain. In fact, what it suggests is that respondents might have some difficulty in comparing behaviours and understanding their individual contribution towards energy savings. Finally, EP respondents were invited to provide information on everything they did to save energy, (Q6), (Appendix VI) and the results suggest a good level of knowledge regarding both, efficiency and curtailment behaviours, which could save energy at home. Equally, FGs’ participants were asked for the same type of information, with the results being presented in Figure 7-6, listing all of these behaviours that were discussed during the FGs.
  • 172. 7. Factors influencing energy use at home 152 As Figure 7-6 shows, during the FGs a number of energy efficient behaviours have been discussed and the majority of the FGs’ participants were able to identify the best practices under specific contexts. However, some respondents at the same time, seemed to lack the level of knowledge, (Q8, Q31), that would enable them to compare different specific behaviours, or to evaluate the saving potential they could achieve. FGs’ participants and CID and PID interviewees strongly agreed that not knowing the individual contribution of energy consuming behaviours could influence the adoption of more energy efficient behaviour. In summary, interpreting the data collected, within the EP, FGs and CIDs, regarding the level of information held proved to be difficult, as well understanding how far a lack of knowledge, could be considered as a barrier. At first glance, there seems to be, what is well known from the literature, an information-behaviour gap, (Jackson, 2005; Schultz, 2002; Southerton et al., 2011; Stern, 1999), since people report a high level of knowledge on the different subjects discussed, but then do not seem to act in accordance. Findings, have however, also shown that once looking at a more specific aspect, or more detailed information, it appears that knowledge and information are not barriers as such, but rather a convenient excuse for not taking action. Such findings are equally known from the literature, with previous research highlighting that people tend to verbalize an inability to do something, (Baker and Kirsch, 1991), as a way to deny personal responsibility for dealing with a problem. In the majority of cases, a general need for being provided with targeted and useful information, that could support individual decision and close information circles, could be observed across the different research phases. 7.2.3 Cultural-normative-social barriers The evolution of cultural and social norms influence energy use at home and thus, can act as a barrier to the adoption of more energy efficient behaviours, (see 3.3.4). This is to say that adopting more energy efficient behaviours, might, challenge existing ways of thinking and doing: the social customs and ways of living and the assumptions that support these attitudes and behaviours that as a consequence represent cultural, normative and social barriers to change. During the FGs, a number of examples of cultural-normative and social barriers could be identified. First of all, the fact that social norms seems to accept a level of energy use without being perceived as overuse. Many FGs’ participants defined their energy use as being usual, habitual, or normal and thus showed no actual need to save energy; FGs’ participants seemed to be quite
  • 173. 7. Factors influencing energy use at home 153 comfortable with how society will judge their energy use. An exception to this normal energy use was discussed by a few FGs’ participants, who reported the pressure from society to reduce energy use and to behave in a way, outlined by the participants as being green, in order to fit the social norm. Those FGs’ participants equally expressed that this perceived need of being green, might even result in reporting things that they do not actually do in order to fulfil the social expectations: “To fit the society norm people say I save, I do all but in reality they do nothing”, Female FG7 As an example of how social norms can influence individual behaviour, FGs’ participants frequently highlighted two cases: recycling and saving energy. They felt that for recycling, the social norm expected one to recycle, while for energy saving this was not the case. For energy, the majority of the FGs’ participants and all three CID interviewees reported to feel somehow entitled to overuse energy and admitted an egoistic focus, i.e. a focus on fulfilling individual needs the way they wanted. Overall however, the question of what could be understood as normal use of energy remained unanswered. This topic was thus further explored during the ID with both, energy consumers, (CID) and energy intervention providers, (PID). CID interviewees were asked to choose one of five alternatives, (high, normal, average, reduced and conditioned), that could best describe their energy use at home. Those five categories were chosen in order to use the terminology that FGs’ participants used during their discussion when they described their energy use at home. Two out of three CID interviewees considered their energy use as average and one as normal, which mirrored the FGs’ results. During the CID interviews it was possible to underpin, to a certain degree, this understanding of normal and average. CID interviewees evaluated their energy use as normal, or average, in comparison to what their friends and family used, as well as how much they paid for energy. Normal or average energy use was additionally defined by all three CID interviewees, through a self-evaluation process by comparing what they did to what they know the best practices were. Yet, normal energy use also seemed to equal minimum energy use. Once asked about what could be seen as the possible minimum energy use at home, CID interviewees enumerated a number of situations that were also perceived by them as being current normal energy usage, such as having a reasonable amount of light, room temperature, or the number of showers required to feel clean.
  • 174. 7. Factors influencing energy use at home 154 In summary, from a consumer’s point of view, there seemed to be an understanding that their energy use is in line with that of their friends and family, therefore it is seen as being normal. PID interviewees reinforced the perception that people will base their understanding of normal use on the amount of energy used, on a daily basis, to fulfil their needs. One of the PID interviewees highlighted this perception of normal use as being influenced by society and current lifestyles. Two of the PID interviewees further highlighted the need of defining normal energy use, taking into consideration the different variables that influence energy use at home, whilst, latterly, being able to communicate these to the consumer. 7.3 Individual psychological factors as a barrier Individual psychological factors such as comfort, habits, willingness, laziness, resistance to change, self- indulgence, or actions that individuals have been already taken at one point in time, are all potential barriers towards to the adoption of more energy efficient behaviour and are discussed below. 7.3.1 Habits as an obstacle to the adoption of more energy efficient behaviours Habits and practices are considered to influence energy use, in both ways, i.e., if bad habits exist they will increase energy use, or good energy habits will decrease use, (see 3.4.1.). FGs’ participants and CID interviewees shared an understanding that a great number of behaviours are habitual in nature and impact their daily life, as the following quotes exemplify: “Human beings are creatures of habits, regardless whether you like it or not (…) people get used. Human beings are creatures of habits, it's a routine”, Female, FG2 “It's really an habit, I enter a room and I switch the light on, I could go back and switch the one before off but I don't and I go further on like this”, Female FG4 “I simply forget it, (to switch appliances really off avoiding standby consumption)”, Female FG7 Habits and practices were perceived as being acquired over time and performed in an automatic way, highlighting the habitual character of energy related behaviours:
  • 175. 7. Factors influencing energy use at home 155 “There are habits that are easier to change than others”, Female, FG2 “Those are habits, some people like to switch lights on”, Male, FG4 “I didn't have that habit, but I started switching appliances really off to avoid standby consumption”, Female, FG7 The majority of the FGs’ participants agreed that adopting more energy efficient habits might be hard to achieve, and even if managing to do so, it was felt that this would lead to a reduced impact in terms of the energy that was used, or saved. Once approached on this topic, some of the FGs’ participants highlighted that they were well aware of some undesirable habits that would lead to higher than necessary energy use, such as showering practices, having the TV on even if not watching it, or not switching the lights off once leaving the room. Though being aware about such undesirable habits, almost all of the participants still found it hard to change them. In their view changing habits would require an individual effort of remembering and repeatedly performing the desirable practice. “We as human beings develop habits which are later on hard to renounce or change”, CID2 Three main reasons were provided, during the FGs and the ID interviews, for the difficulty of changing habits. First of all, most of the FGs’ participants reported the general difficulty in changing any type of habit and this is well reported in literature, (IPPR, 2009; Green Alliance, 2011). This was seen to be particular true when the overall objective was to save energy by engaging in numerous individual actions that, individually, only result in minor monetary savings for each action. Secondly, FGs’ participants and CID interviewees agreed that habits provided a level of comfort, convenience and well-being, that allowed them to be lazy and self-indulgent, repeated what they are used to doing and what seemed to work, again these findings are well in support in literature, (see section 3.4.1.). This resistance was found in almost all established behaviours during the FGs and CIDs. However, resistance was particularly predominant on changing the number, duration and temperature of showers, heating rooms during winter, avoiding standby consumption or switching lights off:
  • 176. 7. Factors influencing energy use at home 156 “No, I don’t close the water once washing myself. No, I open the water, in the meantime I get undressed the water is running to get the right temperature, I get in and the water keeps on running”, Female5, FG2 Male2: If someone would tell me that in the summer I could only have one shower…I would be very disappointed… Male3: no for me it’s also a question of duration…I take ages in the shower, it’s one of those things that make me feel good. Male2: but do you close the water once washing yourself? Male4: no Male2: why? Male4: because of convenience, self-indulgence, FG3 Thirdly, and related to this resistance of changing habits, the majority of FGs’ participants and CID interviewees revealed scepticism regarding the impact of changing such habits in terms of the saving potential that could be realized and, as will be discussed in more detail in section 7.2.3., on self-efficacy and expectations regarding the outcome of own behaviour. However, it could also be observed that a constant awareness of some of the FGs’ participants, might eventually lead to an unfreezing of old habits, as described by Giddens (1984), that would allow for new habits to form. “My conscience is already saying, no, go back and switch that light off”, Female FG7 Nonetheless, some of the FGs’ participants, and of the CID and PID interviewees, agreed that if one could see the impact of habits on the energy bill, then this could facilitate individual behavioural change: “If someone would explain and prove to me that changing an old habit will have a significant impact on my energy bill and on the environment I don't think it would be too complicated to change”, CID1
  • 177. 7. Factors influencing energy use at home 157 During the FGs and CID interviews, a group of participants and interviewees could be identified that seemed to think and act in a different way. This group appeared to behave more often in a more energy efficient way, as a consequence of the way they were educated and raised from an early age. One of the CID interviewees explained the difference between her and her partner’s energy use and that this was related to the different education that they received in their parents’ home, which would have influenced and remained into adulthood. All three CID interviewees argued that some habits, such as leaving light on/off, was something they got used to doing from an early age and that those habits remained over time becoming perceived as normal. For those already used to saving energy, not saving was considered to be irrational, a waste. This could be a reason for an overall agreement, among FGs’ participants and CID and PID interviewees, towards an effort to educating younger generations, to enable them to understanding the impact of their behaviours and positively to help in educating a more energy and environmental responsible generation. The above discussion shows that habits seem to play an important role in energy use at home and are part of one’s narrative once discussing the topic. Participants used habits to justify doing things the way they do it, be it positive or negative and these habits need to be taken into consideration when promoting the adoption of more energy efficient behaviour. 7.3.2 Comfort and convenience Maintaining current levels of comfort seem to be fundamental to FGs’ participants and CID interviewees. Saving energy was often perceived as impacting current levels of comfort, or as one of the PID interview suggested, interventions should be rather targeted at promoting energy conservation, thus avoiding energy wastage, instead of focusing on saving energy, as this is often associated with losing comfort. This relationship between saving energy and a reduced level of comfort, were predominant responses within FG1, FG2 and FG3, where participants seemed to have more disposable income to spend on energy and as a consequence, were willing to trade-off comfort and wellbeing, for more energy use and less savings. This is also known from literature, as the impact of saving energy, on disposable income, might be insufficient to motivate individual action to save energy, since, for example BPIE’s research (2011), suggests that for most households, energy bills account for a small, (3-4 percent), share of their disposable income and thus
  • 178. 7. Factors influencing energy use at home 158 constitutes a barrier for meaningful action towards reduced energy use. However, a distinction could be seen during the FGs and the ID interviews, between behaviour that could impact comfort and those that were just inconvenient to do. Examples of comfort reduction included reducing shower duration, or room temperature, with examples of inconvenience being the need to get out of bed to really switch the TV off, instead of leaving it set on standby mode. Several FGs’ participants felt strongly that convenience could be linked to laziness and self-indulgence, in the sense that it was more convenient to leave appliances on, instead of really switching them off and later, on again. Overall, there was a tendency to consider family wellbeing as more important, than the financial or the environmental impact for saving energy. In particular, for those cases where FGs’ participants were parents, their children were reported as having a significant impact on the energy use at home and this does not always mean using energy in an unsustainable way. This influence starts at an early age, with parents reporting the need for installing/improving their heating systems, or of increasing room temperature, in order to maintain family wellbeing: “At home we only installed a heating system once our child was born”, Female, FG7 However, having children at home seems to have a higher influence, once children get older and adopt less energy efficient behaviours, such as leaving the lights, computer or TV on as well as having longer showers. This connects back to the need for educating this, new, generation, in order to better understand the impact their behaviour can have and promoting the development of more energy efficient expectations. Overall, comfort and convenience appeared to constitute a clear barrier towards reducing energy use at home, which is also known from literature as being a strong reason, (e.g. Barenergy, 2011, Darnton, 2008, Darnton et al., 2011, Jackson, 2005, Prendergrast et al., 2008). 7.3.3 Efficacy and outcome expectations The initial findings from the EP survey questionnaire suggested, that respondents held a low level of self- efficacy towards the adoption of more energy efficient behaviours, with more than half of EP respondents reporting to already be doing everything they can in order to save energy at home and with 22.1 percent reporting that they, “Save already enough”. In contrast, the majority of FGs’ participants and CID
  • 179. 7. Factors influencing energy use at home 159 interviewees, when asked if they agreed with such a statement, rejected that they could be already doing everything they can do to save energy at home. Most FGs’ participants strongly felt, that there is always something one can do to save energy at home, which indicates a level of self-efficacy regarding their potential to save energy at home. However, this opinion gradually changed during the FGs’ discussion, when the discussion moved from the abstract level of saving energy, to specific behaviours that were explored in more detail. When asked for the reasons for not saving more energy at home, a number of the FGs’ participants used their existing energy saving behaviours as a reason for not saving further. As such, reporting to already act in a more energy efficient way, apparently, provided a feeling of indulgence that justified no need to take further action. The findings from the EP, show that 16.9 percent of respondents claim that they would like to do more, but do not know how, while only 2.3 percent do not believe their efforts towards saving energy would be worthwhile. In contrast to the EP findings, the majority of the FGs’ participants and CID interviewees appeared to be confident regarding their ability to adopt more energy efficient behaviours, with emerging narratives revealing that they were, nevertheless, unsure regarding the outcome of such behaviour in terms of energy used and saved. During both, FGs and CIDs, there were no significant differences regarding the topic that appeared to be noteworthy. Some of the reasons, for such disbelief, on the outcomes provided by FGs and CIDs include, the need for collective action and that individual responses alone would not be sufficient. As one FG participant summarized it: “I can know how to perform more energy efficient behaviours, but if the remaining family members don’t do the same them his effort might be easily cancelled off.” Male, FG3 For all of the FGs, though to a varying degree, the discussion seemed to move from a question of being able, to being willing to adopt more energy efficient behaviours, when comparing individual and collective efforts. Being able and being willing, seemed to be aligned when discussing change in the easy and simple, rather than difficult and complicated behaviour. In terms of saving energy, as something easy and simple to do, meaning just a matter of changing habits, appears to be valid for those day-to-day actions that do not require much effort to perform and that do not impact on the level of comfort and wellbeing at home. FGs’ participants provided some examples of such behaviours that they reported to be willing to change namely, switching lights off, cooking with the lids on and reducing the number of times and duration of opening the
  • 180. 7. Factors influencing energy use at home 160 fridge. Avoiding standby consumption was not always reported as being easy, since there is a convenience factor attached to the behaviour that was reported as hindering best practice. The perception of behaviours that were difficult to change included those that were directly associated with perceived and desired levels of comfort and wellbeing, such as reducing room temperature or reducing the number and duration of showers. This question of evaluating how easy, or difficult, it would be to save energy, was further explored during the ID interviews where interviewees were asked how easy, or difficult, they found energy saving at home to be. CID interviewees were divided, with two reporting it to be difficult and one considering it moderately easy. Once asked to explain their choice, CID interviewees provided a list of reasons for energy savings to be considered difficult to achieve, namely, existing ingrained habits, unwillingness to change those habits, the need to invest in order to realize significant savings, the focus on maintaining comfort levels, as well as the fact that individual efforts can be negated by other family members’ non-saving habits. Similar answers were reported by PID interviewees that considered energy saving as something easy to achieve, or at least to reduce the amount of wasted energy, but simultaneously, also as something difficult to achieve. PID interviewees argued that people do not hold enough information in order to understand and realize their energy savings in terms of their energy bills and as a consequence, this could lead to the abandonment of energy saving behaviours, in particular where previous, negative energy saving experiences could work as a barrier towards future energy saving attempts. With regards to information, knowledge and self-efficacy, the PID assumptions were aligned with EP and FGs’ responses that they felt they had, overall, a good understanding on how to save energy, including the behaviours that might need to be changed to save energy. In summary, it might be inferred from the findings that EP respondents, FGs’ participants and CID interviewees, overall hold a good level of knowledge, that could help them adopt more energy efficient behaviours and as such, appear to believe they have the ability to adopt those behaviours it they want to, but, that for some reason, they resist and are unwilling to doing so, as explored further in the following section.
  • 181. 7. Factors influencing energy use at home 161 7.3.4 Resistance to and unwillingness to change During the FGs and CIDs, an apparent resistance and willingness to change could be observed amongst the interviewees and three broad reasons could be identified for this. Firstly, the majority of the FGs’ participants and all three CID interviewees reported a disbelief regarding the outcomes of their actions, notably on the amount of energy that could be indeed saved, by adopting more energy efficient behaviours. FGs’ participants and CID interviewees expressed an overall frustration, regarding the outcomes of previous behaviour change attempts in order to save energy at home. Not being able to realize the outcome of their savings, was reported by the majority of the FGs’ participants and by all three CID interviewees, as influencing not only the abandonment of the newly acquired behaviour, but also as influencing future attempts to save energy, as they felt discouraged by such attempts: “I stopped doing so, (unplugging appliances and switching lights off), since the invoice went up once I was doing it (…)…I got disappointed and currently I just don't care, I do my normal use”” Male, FG7 “My individual perception is that by switching the light off 20 seconds before won’t solve my problem of reducing my energy bill”, CID1 These quotes highlight the low outcome expectancy associated with curtailment behaviour. During the FGs, it was possible to observe that expectations were apparently different, once it came to efficiency behaviours that required an investment in more energy efficient solutions. This is to say that the expected energy savings that could be realized through day-to-day curtailment behaviours were perceived insignificant or low, when compared to the, perceived, saving potential that could be achieved through investments, such as buying energy efficient appliances, investing in renewable energy sources, or even by moving into a different house. However, the majority of FGs’ participants and all three CID interviewees were aware that realizing such outcome expectations, through efficiency behaviours, would require surpassing a set of financial and technical barriers. A second reason appears to relate to the individual effort that is required to maintain those behaviours, as well as to promote them within family members. This seemed to be in particular important for those FGs’
  • 182. 7. Factors influencing energy use at home 162 participants and CID interviewees, whose family members were not supportive with regards to more energy efficient lifestyles at home. During the FGs and the CID interviews, a number of examples were provided, such as the use of TV and PlayStations, or leaving lights on, once not in use. It also could be observed that family members either reinforced, or served as a driving force, to save energy, or in the opposite direction they behaved in a way that would increase energy use. These different points of view hold the potential to cause stressful situations at home and are in particular evident in parent-child relationships, with two FGs’ participants reporting threatening to adopt extreme measures, like switching warm water off, if their children spend too much time under the shower. Those FGs’ participants and CID interviewees with unsupportive family members reported either to be willing to make an additional effort to convince other family members to use less energy, or to just accept what the remaining family members did in order to avoid conflict. This feeling of being alone in their individual efforts to save energy relates to the third observed reason, unwillingness to adopt more energy efficient behaviours; where individual efforts were perceived as having only a small impact and that they would require a collective effort, from the remaining family members, as well as society in general. The majority of FGs’ participants and CID interviewees reported believing their behaviours have little effect impact on the environment, without collective effort. This is mirroring findings in Kaplan (2000), on the potential impact of one’s contribution and the perception of helplessness and personal sacrifice. During the FGs and the CID interviews, this feeling of being alone in their individual efforts, was often reported to exist within the participants’ households, e.g. between partners and parents- children relationships, but also with the majority of the FGs’ participants, who reported the feeling that saving energy is not a widespread practice among society. For this reason, doing something that others were not doing was reported as a discouragement to their attempts to save energy, because singular activity was not felt to be worthwhile, or effective, with an overall tendency for FG participants to ascribe the responsibility of saving energy to others, namely neighbours, local and national government or, perceived, big polluters, such as industry: “Our first example should come from the government. If they don't do it, (talking about saving energy), why should we do it?” Female, FG7
  • 184. 7. Factors influencing energy use at home 164 Table 7-2 – Summary of findings relating to RQ2. Empirical study findings RQ Noteworthy further observation Chapter Section: 7.1.Relation of behaviours and energy use Chapter Section: 7.1. Motivational variables and energy efficient behaviours 7.1.1. The motivation for saving money Saving money as the most reported motivation to saving energy. RQ2a, RQ2b There appears to be a misconception regarding the concept of saving, with saving energy being interpreted as saving money. While cost-savings have been reported as the most important motivation, it could be equally observed that monetary motivation appeared to be in direct conflict with curtailment behaviours that would be required to actually realize such monetary gains. RQ2a, RQ2b The motivation to save for monetary reasons seems to be even more important to those that appeared to have a lower level of disposable income. Direct and indirect rebound, with financial saving being used in energy and carbon intensive behaviours, reducing the environmental benefit achieved through the energy saved. RQ2b Misconceptions, in terms of individual behaviour, that could save energy without necessarily impacting the environment, i.e., the use of home appliances during the off peak tariffs and the use of wood as a way to save energy. 7.1.2. Pro-environmental and pro-social motivations Positive attitudes towards energy saving seemed to be surpassed by the direct, individual, benefits of energy use, such as comfort and wellbeing. RQ2c In isolation, environmental and energy conservation, might be strong motivational variables, but comparatively weak when in conjunction with other variables such as comfort and convenience. Attitude-behaviour gap: pro-environmental attitudes seem to have little predictive power to explain energy use at home. RQ2c Understanding that today’s generation would not suffer the consequences of predicted and forthcoming environmental problems.
  • 185. 7. Factors influencing energy use at home 165 Empirical study findings RQ Noteworthy further observation 7.1.3. Needs and expectations and its relation to motivation for saving energy Current energy use perceived as socially acceptable, with people’s behaviour aligned to what appears to be the social norm and expectations regarding the fulfilment of individual needs. RQ2b, RQ2c Chapter Section: 7.2. Barriers for adopting more energy efficient behaviours 7.2.1. External/macro barriers: policy based, structural and economic barriers Policy based barriers: need for product standardization and development of penalty/incentive schemes. RQ2c Physical-structural barriers: infrastructure of the house, as well as existing home appliances. RQ2b, RQ2c Evidence of the lock in effect: changing existing infrastructure will be cost intensive and only feasible in the medium-term. RQ2b, RQ2c Reduced availability to invest in more energy efficient solutions. RQ2b 7.2.2. Knowledge based barriers Lack of information, as the most commonly reported barrier to save energy at home. RQ2b Misconception regarding the use of off peak, as a way to save energy.
  • 186. 7. Factors influencing energy use at home 166 Empirical study findings RQ Noteworthy further observation 7.2.2. Knowledge based barriers (cont.) Existing lack of information with regards to: (1), overall energy use, (2) the contribution of specific home appliances and behaviours to total amount energy use, (3), the amount of energy that can be saved by adopting more energy efficient behaviour. RQ2b, RQ2c No clear understanding of how far this lack of information is a barrier towards the adoption of more energy efficient behaviours. There seems to be an information- behaviour gap and people do not act in accordance to their reported level of knowledge, but less certainty exists once looking at specific behaviours where there appears to be the need for further information. Apparent difficulty when comparing behaviour and in understand their individual contribution to energy savings. Acknowledged difficulty in understanding the relation between individual energy use and environmental damage, which together negatively influenced individual motivation to save energy (see 7.1.2). Strong agreement that knowing the individual contribution of energy consuming behaviour could influence the adoption of more energy efficient behaviour. Understanding of energy in monetary terms rather than energy units, which increase the difficulty of understanding the difference in energy use to the price of energy. RQ2b, RQ2c No clear understanding whether denying to not being able to save energy, is a strategy to deny personal responsibility. The understanding of normal energy use is required for better understanding individual energy use. RQ2b, RQ2c 7.2.3. Cultural-normative-social barriers Cultural and social norms were perceived as influencing the normal way of using energy at home and as such, set the limits to change and adoption of more energy efficient behaviours and practices that were perceived as not desirable. RQ2b, RQ2c Adopting more energy efficient behaviours might challenge existing ways of thinking and behaving: the social customs and the way of living. RQ2b, RQ2c Social norm seems to accept a level of energy use, without being perceived as overuse. RQ2b, RQ2c
  • 187. 7. Factors influencing energy use at home 167 Empirical study findings RQ Noteworthy further observation Chapter Section: 7.3. Individual psychological factors as a barrier 7.3.1. Habits as an obstacle Most energy related behaviours are of a habitual nature and acquired over time. RQ2b, RQ2c Reasons for adopting more energy efficient habits as hard to achieve include: (1), remembering to do the right thing, (2), habits provide a level of comfort, convenience and well-being that allows for lazy and self-indulgent behaviour, (3), scepticism regarding the impact of these habits in terms of home energy use. RQ2b, RQ2c Early influences on energy use appeared to be critical in developing habits that are learnt and embedded. 7.3.2.Comfort and convenience Saving money, or the environment, enters into competition with comfort and convenience. RQ2b, RQ2c Overall tendency for considering family wellbeing as more important than the financial, or environmental, impact of saving energy. RQ2b, RQ2c 7.3.3.Efficacy and outcome expectations Good reported levels of overall efficacy expectations, with different efficacy expectations depending on the behaviour under discussion. RQ2b, RQ2c Low level of outcome expectations, not only with regard to the amount of energy that can be reduced, as well as the need for collective effort in order to be meaningful. RQ2b, RQ2c Feeling of helpless and ineffectiveness of one’s own contribution that start at home, since it was often reported to be an individual effort and not shared by all family members, which reduced even further, the attempts to save energy within the household level unit. Reporting to already act in a more energy efficient way, apparently provides a feeling of indulgence that justifies a perception of no need for further action. RQ2b, RQ2c Efficacy increases for easy to do things that have no real impact on comfort and wellbeing levels. RQ2b, RQ2c
  • 188. 7. Factors influencing energy use at home 168 Empirical study findings RQ Noteworthy further observation 7.3.4.Resistence and unwillingness to change Resistance to and unwillingness to change often appear to result from: (1), low outcome expectancy, associated with curtailment behaviour, (2), individual effort that is required to maintain those behaviours, as well as to promote them within the family members and (3), individual efforts perceived as having a small impact, that would require a collective effort, from the remaining family members, as well as society. RQ2b, RQ2c Findings suggest that adopting more energy efficient behaviour doesn’t appears to be a question of ability, but rather of willingness of doing so, which relates to outcome expectations, both in terms of energy saved, as well as the need for collective action.
  • 189. 8. Intervention strategies and perceived effectiveness 169 As can be seen from this chapter, the barriers reported within the energyprofiler survey questionnaire, (EP), focus groups, (FGs) and in-depth individual interviews, (ID), outnumbered motivations to reducing energy use at home. In addition to this, the motivations that have been presented did not appear to result in actual energy use reductions. Positive attitudes towards energy saving, appeared to be surpassed by the individual direct benefits of energy use, such as comfort and wellbeing. Equally, monetary motivation appeared to be in direct conflict with curtailment behaviours that would be required to actually realize such monetary gains. Thus, motivational variables appeared to be in direct competition with the barriers, such as reduced convenience and comfort. These findings support well the literature that had been presented in chapter 3 and thus support earlier results from Barenergy (2011), Darnton (2008), Darnton et al. (2011), Jackson (2005) and Prendergrast et al. (2008). The results do show however, that reported barriers are perhaps not actual barriers, but in part a convenient excuse, exemplified by the information-behaviour gap, (Jackson, 2005; Schultz, 2002; Southerton et al., 2011; Stern, 1999) This supports the earlier findings from Baker and Kirsch (1991), that people tend to verbalize an inability to do something, as a way of denying personal responsibility in dealing with a problem. This could also be observed with regards to efficacy and outcome expectations, which as such, did not appear to be a major barrier. Notably, the findings from the FGs showed that the question is perhaps, less about being able to adopt more energy efficient behaviours and more about the willingness to do so. Thus, the overall results from this chapter reflect the literature findings presented in chapter 3.
  • 190. 8. Intervention strategies and perceived effectiveness 170 8 Intervention strategies and perceived effectiveness Chapter eight explores the perceived effectiveness of different intervention strategies and the potential effectiveness of change interventions within the field of energy use at home. The chapter discusses the findings from the energyprofiler survey questionnaire, (EP), the focus groups, (FGs) and the in-depth individual interviews, (ID), regarding the findings on the role of intervention strategies in energy use at home, (RQ3). Intervention strategies and their perceived effectiveness, in encouraging the adoption of more energy efficient behaviour, were initially explored during the FGs, with participants being asked to propose specific interventions that could be launched nation-wide in order to encourage the adoption of more energy efficient behaviour at home. The topic was further explored, within the CID and PID interviews, in order to better understand what future interventions might look like. Figure 8-1, shows the type of interventions discussed during roundtable discussions and how FGs’ participants perceived that these interventions could address barriers to the adoption of more energy efficient behaviour at home. Data regarding the types of intervention have been extracted from FGs’ transcripts, with follow up discussion identifying barriers where intervention could be addressed. Figure 8-1: Type of interventions in relation to the barriers that could be addressed. Type of Intervention FG1 FG2 FG3 FG4 FG5 FG6 FG7 Monitoring systems (e.g. energymeters) .. .. ... . ... ... Education . . .. .. . .. .. Prompting .. .. .. .. Benefit vs. Penalty .. . . ... .. Provision of financial incentives .. . . . Provision of simple comparative terms (e.g. home appliance) . .. .. Comparison to other people . . Provision of general information on how to save energy at home . . . . . . . Provide an average, normal energy use value ... ... ... ... Demonstrate good practices/Model behaviours ... ... . .. .. Inclusion of smart features in the home appliances . . . Provision of simple examples at the energy invoices .. . Provision of information at the point of sales . . . . Provision of tailored information (e.g. energy audit) .. .. . .. Provision of free samples . . . . . . . Labelling of products .. .. .. ... .. Barriers: Inability to measure energy use|Lack of information|Initial investment cost | Habit | Invisibility | Social norms
  • 191. 8. Intervention strategies and perceived effectiveness 171 As can be seen from Figure 8-1, education, provision of general information, or the provision of free samples, have been put forward by each of the 7 FGs as suitable interventions. Similarly, the use of monitoring systems, benefit vs. penalty type schemes, demonstration of good practice, as well as the provision of tailored information, including labelling of products, were seen by FGs’ participants as possible interventions that hold high potential for encouraging the adoption of more energy efficient behaviour. These will be looked at more in detail through this chapter. Further, as can be seen from Figure 8-1, FG1, FG4 and FG5 are minimally populated, in terms of type of interventions discussed, when compared to others. This could only be seen while compiling the data and as such, the reasons for this have not been directly explored within the FGs. However, each FG had specific characteristics, with FG1 composed of participants that work within the energy efficiency field, that hold a consistent opinion regarding the effectiveness of the different types of intervention. This might be a reason for them discussing a reduced number of intervention types, that they perceived as most effective and worthy of mention. Regarding FG4 and FG5, participants seemed to hold a lower purchasing power, as well as a lower education level, which may contribute to a reduced set of intervention alternatives that, in particular, target the financial component of energy use. In this chapter, the nature of Intervention strategies discussed by research participants and their perceived effectiveness, will be presented in more detail. 8.1 Communication design and persuasion As can be seen from the literature, persuasion can influence others, (Jackson, 2005; Martiskainen, 2007; Simons, 1976, p. 21) and is often dependent on the credibility of the sender, the persuasiveness of the argument/message, or the responsiveness of the audience, (O’Keefe, 1990). Thus persuading people to change can be particularly difficult, (Jackson, 2005). Therefore, one objective of the FGs was to further explore the perceived requirements for communication design and persuasion. FGs’ participants were asked to recall campaigns promoting energy efficient behaviour and subsequently, were asked to design, for themselves, a communication and information campaign on how to promote the adoption of more energy efficient behaviour.
  • 192. 8. Intervention strategies and perceived effectiveness 172 With regards to communication design, in four of the FGs the general importance of the message sender was stressed and that they need to be both reliable and able to create empathy with the targeted audience. The FGs’ roundtable discussion brought up a number of examples of what could be considered a reliable and persuasive sender, with overall agreement towards ordinary people, known actors or TV reporters and children. Messages issued by utility companies were considered helpful, but potentially less effective since they could lead to confusion and distrust. FGs’ participants pointed out confusion when receiving advice from their electricity supplier to save energy, as this was perceived as reducing their own business. In addition to this, it was stressed that the message/argument needs to be persuasive, in order not to be rejected or ignored, as a way to avoid confronting implications for appreciated energy inefficient behaviours, as postulated by Upham et al., (2009). Further to this, an overall agreement could be seen among the majority of FGs’ participants and ID interviewees, that persuading people to adopt more energy efficient behaviour would be challenging to achieve, in particular for less easy, or simple behavioural changes or, those that were perceived as impacting desired normal levels of comfort, convenience or wellbeing. It could not be found however if messages promoting such undesired and unpopular energy efficient behaviours could actually not backfire and highlight the prevalence of energy inefficiency as a habit shared by other people. This, apparent, individual unwillingness to address comfort and wellbeing levels was shared across FGs’ participants, CID and PID interviewees and it is uncertain how successful future interventions could be that target such a focus. Findings from this research suggest rather that promoting the adoption of more energy efficient behaviour, perceived as having undesirable consequences, could lead people to not doing so. This situation is known in the literature as a, ‘confirmation bias’ where people look for information that is consistent with what they already think, want, or feel, leading them to avoid, dismiss, or forget information that will require them to change their mind-set and, quite possibly, their behaviour, (Shome & Marx, 2009); where, “I can’t”, simply means, “I don’t want to”. Findings from the FGs and IDs overall suggest that an individuals’ positive attitudes towards comfort and wellbeing, are stronger than attitudes towards the environment and as such, there might not be any emotions, such as disappointment, dissatisfaction, shame, embarrassment or guilt, that could help lead to the adoption of more energy efficient behaviour. Therefore, interventions that would draw from persuasion theories, (section 4. 2) and that use judgment, cognitive dissonance or self-
  • 193. 8. Intervention strategies and perceived effectiveness 173 discrepancy methodologies would not be perceived as persuasive, or potentially effective, with regards to triggering the desired response from the audience. 8.2 Structural interventions 8.2.1 Rewards and punishments A rewards and punishment scheme was discussed within five out of the seven FGs as a way to encourage the adoption of more energy efficient behaviour. FGs’ participants were found open to an approach that would reward those people who underused energy and punished those that over used it. As a pre-requisite for such a scheme, FGs’ participants agreed on the need to define a set of base values for energy use at home, to punish those overusing and reward those underusing energy at home. In accordance with FGs’ participants, a base value for energy use should take into account the amount of energy required to fulfil basic needs; though it was not fully understood what was considered to be a basic need and, similar to the discussions of chapter six and seven, what is understood to be normal. Some of the FGs’ participants suggested this base level of energy use could be provided, either for free, or at a flat rate entrance value, so as to provide an understanding of what is considered an acceptable level of basic energy use at home. This concept of a flat basic and an increasing non-basic rate was compared by some of the FGs’ participants with one that they recalled for water consumption in Portugal, where people paid different prices for water, higher consumption equalling a higher price charged. Yet, even though greeted by initial enthusiasm from the roundtable discussion during FGs, it was not possible to determine how effective such a scheme could be. A number of FGs’ participants expressed an opinion that such a scheme would probably not work, due to a lack of motivation and that people would maintain established practices as long as they could afford to use energy as they do at the present. Despite such concerns, there was an overall agreement that such a scheme should, nevertheless, facilitate the development of a measurable mind set for energy use, as well as being a fair instrument to compensate those people willing to adopt more energy efficient behaviour and to use less energy at home. In contrast to FGs’ participants, PID interviewees did not consider such scheme a viable intervention, although each for different reasons. In PID1, the interviewee from an energy supplier,
  • 194. 8. Intervention strategies and perceived effectiveness 174 argued that such a scheme could backfire since there is, currently, no value to identify what a normal, (average), use of energy could be, as well how to best calculate such value, which could be a complex process to implement and monitor. With PID2, the interviewee from the national energy agency argued that people can only support penalties and punishments until a certain point and that the energy saved should be motivation enough to adopt more energy efficient behaviour. For PID3, the interviewee from the national utility program, preferred to promote adoption of long-term mechanisms that support a consistent reduction of energy demand, rather than random measures focused on specific scenarios. In summary, results from this research suggest that energy users and intervention providers have different opinions regarding the use of reward and punishment intervention schemes. From a user point of view, reward and punishment schemes appear to be evaluated as desirable and a partially effective type of intervention. While from an intervention provider this intervention type does not seem to be that appealing or perceived as effective. 8.2.2 Incentives and samples The provision of incentives, including samples of more energy efficient home appliances, was evaluated as an effective alternative to promoting the adoption of more energy efficient technologies, by removing or reducing the risk energy users would need to take. The provision of samples was discussed within all 7 FGs, with FGs’ participants providing the example of energy efficient light bulbs that were distributed, for free, as part of a national program to reduce the market entrance barriers to the deployment of the new light bulb technologies 15 . FGs’ participants agreed that this distribution of light bulbs, for free, allowed them to experiment and removed the burden of investment for such initial experimentations. In addition to this, FGs’ participants also highlighted the low personal effort that was required to get their sample light bulb: “One only needed to exchange the light bulbs…they even sent one to home”, Male, FG7 “I got them for free, it was a bonus… they were giving them away at the supermarket”, Male FG4 15 The distribution of more energy efficient appliances was financed through a Portuguese National Fund aiming at promoting energy efficiency within the residential, services and industry sectors. More information available at www.erse.pt
  • 195. 8. Intervention strategies and perceived effectiveness 175 Based on such positive experience, FGs’ participants suggested that the government could promote similar interventions for other home appliances, as well as renewable energy sources, as a way to reduce the initial investment required in purchasing more energy efficient appliances. Even though there were, at that time, other type of financial incentives to adopt more energy efficient home appliances or renewable energy sources, only a reduced number of FGs’ participants were aware of such incentive schemes. Within subsequent PID interviews, interviewees were, nevertheless, reluctant towards such types of intervention, with two out of three interviewees criticizing the unfairness in distribution that frequently accompanies the sample, or incentive provision. As a concrete example, PID2 referred to the energy efficient light bulbs, where the criterion of receiving one was to have lower average bills, resulted in light bulbs being repositioned to holiday/second homes. In addition to the unequally/unfair distribution, PID3 had a general concern that supplying energy efficient appliances, for free, could promote the introduction of more energy efficient products that are at an early stage of technological maturity, which could lead to a lost opportunity of promoting the technology in the future, if the first user experience is negative. 8.2.3 Labelling During the FGs’ roundtable discussion, a frequent narrative emerged, centered around the discussion of A rated home appliances being better than others. Nevertheless, during FG1, those participants working in the energy area, suggested that people in general do not understand the scope of energy rating labels, are unable to compare the performance of different home appliances and that as a result, they do not know how much energy they will, potentially, consume, or save. This view was common across the other FGs in two different ways. First of all, during the FGs there was no discussion comparing other characteristics such as size, load capacity, or use pattern, that influence the amount of energy used and that would demonstrate FGs’ participants understanding the impact of their purchasing decision. Rather than questioning if one needs a bigger fridge or washing machine, the notion was that as long as it is, ‘A rated’, it is energy efficient and as such, it is a good purchase. Secondly, a few of the FGs’ participants recommended that all non A-rated home appliances should be banned from the market as an alternative, to release consumers from the need of trying to compare the different available options. During the FGs it was not possible to fully understand if this was a strategy to promote sustainability, or rather translating into the
  • 196. 8. Intervention strategies and perceived effectiveness 176 difficulty FGs’ participants might have in understanding the information provided by the labels, though it could equally have been an example for choice architecture, as will be further discussed in section 8.2.5. Findings do, however, question the effectiveness of labels. Even though labels apparently provided meaningful and easy to understand information, it was not clear that the use of standardized labels across products would indeed lead to better informed purchasing decisions and, in particular, for those consumers that lack motivation and knowledge to compare different solutions, in terms of purchase and later use. This might be one of the reasons for some FGs’ participants reporting looking for information at the point of sale, as well as from the shop staff. Shop staff appeared, during the FGs and the CID interviews, to be perceived as a trusted source of information to facilitate the purchase of more energy efficient home appliances instead of, or in combination with, energy labels. One PID interviewee even extended the discussion to the home energy performance certificate 16 , an energy label for homes and questioned whether people would pay much attention to the energy class of the house, or whether other variables would be of a higher relevance to the buyer, such as the house location. The PID interviewee questioned the impact of such a certification due to, their, individual understanding that people mainly request the certificate to comply with the law if they want to sell/rent a house, rather than being interested in and motivated to adopting the efficiency measures proposed within the certificate. In summary, results suggest that labels could be an adequate intervention type; though it equally appears that an increased level of knowledge might be required to understand the information within such labels. Findings also indicate that it was not understood that the A label alone is only a relative indicator and not to be seen in isolation from the actual day to day usage. Analogous to the literature, findings did indicate that it might thus be a requirement to provide a consistent and comparative level of information for consumers, (DGGE/IP-3E, 2004). With this, findings show that the general challenge for labels was seen to be to ensure that the information provided is meaningful, easy to understand and standardised. Also that consumers are motivated into wanting to take action and thus supporting earlier findings from Southerton et al., (2011). 16 Energy Performance Certificate are today obligatory for homes under the Energy Performance of Buildings Directive - Directive 2002/91/EC, EPBD.
  • 197. 8. Intervention strategies and perceived effectiveness 177 8.2.4 Demonstrating and facilitating During roundtable discussions, FGs’ participants often referred to modelling and demonstration as a way to promote individual behavioural change. FGs’ participants discussed three situation that could be framed within modelling and demonstration: (1), central/local government actions, that demonstrate saving energy is an important thing to do, for instance, by switching street or monument lights off at night; (2), the modelling effect of parents on children, and vice versa. Behaviour adopted within the family home during childhood seem to remain into adult life and, in contrast, parents are influenced by their children and the good practices they learn at school, (e.g. with the recycling practices); (3), demonstration of the benefits of more energy efficient appliances. Some FGs’ participants recalled having seen a comparison, at a point of sale, between traditional light bulbs and more energy efficient ones, placed side-by-side with an independent energy counter attached to each, indicating what amount of energy was being used. FGs’ participants agreed that this allowed them to compare the individual energy consumption of each technology, allowing them to have better informed decisions in a very easy way: “They had a traditional light bulb on with the counter moving and next to it an energy efficient one with the counter moving much slower and one could see it” Female, FG7 Findings from this research suggest that modelling and demonstration was perceived to be an effective type of intervention, with regards to the provision of desirable behaviours and to encourage learning by observing how others behave. Modelling behaviour was also seen as a potentially effective avenue for changing behaviour, as people follow these examples once they are understandable, relevant, and rewarding in terms of positive results.
  • 198. 8. Intervention strategies and perceived effectiveness 178 8.2.5 Intervention through design During the FGs, participants discussed two types of intervention with regards to environmental design and material context adjustment. Firstly, the need to change home infrastructure and appliances towards more energy efficient ones and secondly, the inclusion of smart features, which was perceived as a type of communication/feedback mechanism that could facilitate using home appliances more efficiently With regards to home infrastructure, FGs’ participants and ID interviewees highlighted the fact that the infrastructure of their current homes is not supportive towards using less energy without having to trading- off their present level of comfort. When asked to evaluate their current level of energy use and comfort, and to forecast for the 10 years, all three CID interviewees agreed they would maintain, or increase, their comfort level, whilst potentially reducing energy use by the deployment of more energy efficient appliances and improved home infrastructure. This 10-year period was perceived as sufficient to improve their homes and to substitute existing home appliances with more energy efficient ones, which would lead to a potentially reduced level of energy use without needing to take additional measures. Yet, regarding energy related practices, interventions that were put forward rather focused on improving home infrastructure, or existing home appliances, in order to promote increased savings, but largely neglected interventions aimed at how the home and home appliances are used, and on the impact of everyday behaviour as a way to reduce energy use. With regards to the way products are designed and, in particular, the inclusion of smart features that could facilitate the adoption of more energy efficient behaviours at home, some examples were provided by FGs’ participants, such as the inclusion of sound alerts that would remind people to switch appliances off, comparing this to the system recent cars have to remind you of the need to use the seat belt. This connects with the literature on choice architecture, (Dobson, 2011; Grist, 2010; Southerton et al., 2011; Thaler & Sunstein, 2008), which from a product perspective could, for instance, mean only having a cold wash washing machine, rather than trying to educate people to wash at 30º. Under these circumstances the home appliance itself would take the decision away from the user. FGs’ participants used the standby option as a way to express how convenient and comfortable some of the default options are day-to-day:
  • 199. 8. Intervention strategies and perceived effectiveness 179 “I try, but I have to recognize it’s difficult for me to switch appliances from standby. For example, we are in bed and it’s much easier to switch the TV with the remote control…it’s more comfortable…sometimes I remember but I’m feeling so good in bed that I don’t stand up”, Female, FG6 Within subsequent PID interviews and, perhaps a bit unexpectedly, PID interviewees did not consider such strategies that relate to choice architecture and the concept of nudging, (Dobson, 2011; Grist, 2010; Southerton et al., 2011; Thaler & Sunstein, 2008) and where the default options are set in order to facilitate individual best practice. The reason for such non-considerations did remain, however, unclear. In summary, findings from this research suggest that product design and contextual adjustments could be an effective type of intervention to reduce energy use at home, but that they will not necessarily encourage the adoption of more energy efficient behaviours as such as they are based on a ‘technofix’ approach, (see 2.2.7, 4.3.2). They are perceived as being sufficient and thus release users from the daily effort to adopt more energy efficient behaviour. Adapting product design seems to inhibit the potential for learning and adopting other energy efficient behaviours, other than that relating to the adopted product. 8.3 Psychological interventions 8.3.1 Targeted face-to-face information During the FGs, an overall agreement could be observed with regards to advantages of providing tailored, preferably face-to-face, information and feedback. To illustrate the point, FGs’ participants often described a scenario where someone with knowledge in the area would visit their home, evaluates their energy use, and then provide tailored advice on how they could save energy and on how to account for those savings. Though often not referring to the technical term, FGs’ participants were describing a home audit as a means with significant potential for promoting energy saving at home. The main disadvantage of this type of intervention relates, however, to the time required for such audits and the inherent cost resulting from being human resource intensive, (section 4.4). Providing customized information, through a number of alternatives, was perceived by FGs’ participants as beneficial to better understand what one could do and
  • 200. 8. Intervention strategies and perceived effectiveness 180 how much energy could be saved for the specific individual circumstances, thus reducing the confusion between the amount of information currently available and the difficulty to sort out what is important. FGs’ participants reported difficulty in understanding the available information, comparing the different sources of data, as well as being able to reserve time for doing so. Managing and understanding existing information was often perceived as over-demanding for the majority of the FGs’ participants, since it requires, time, a degree of skill, and a willingness to do so. These findings suggest an overall concern regarding which information is accurate, who to trust in the myriad of actors in the field, from utility companies to NGOs to suppliers of energy efficient products and services, crowned by a simultaneous lack of a reliable voice, without vested interest, in the field of energy related information. From the narratives that were built during the FGs’ roundtable discussion, one could expect that the provision of targeted information could encourage adoption of more energy efficient behaviours yet evidence within this research is mixed, with FGs’ participants being divided. Some of the FGs’ participants agreed that if they knew exactly what to do, they would act in accordance and others reported that at best they would know they are doing something they should not, but would not change existing practices and habits. However, FGs’ participants seemed to be more receptive to personalized information, rather than selecting for themselves what is important or not. For this reason, a face-to-face, tailored, information type of intervention, such as an energy audit might still be an effective type of intervention, to at least impact the level of awareness, regarding more energy efficient behaviour. The impact this type of intervention would have, in terms of generating energy savings, needs evaluation. 8.3.2 Information and communication campaigns During FGs, participants were asked to recall information and communication campaigns that promoted the adoption of more energy efficient behaviour, to discuss their efficacy as well as to suggest perceived requirements that could lead to their effectiveness. FGs’ participants recalled six energy saving campaigns, however, considering the total of 41 FG participants, this could be interpreted as a low number. During the follow up discussion, FGs’ participants appeared to be less aware of energy related campaigns, compared to other pro-environmental fields such as recycling.
  • 201. 8. Intervention strategies and perceived effectiveness 181 Most of FGs’ participants provided a positive evaluation towards the role that communication and information campaigns can play, in terms of providing information and raising the awareness about more energy efficient behaviour. However, they were less certain of how effective these campaigns were in persuading people to adopt more energy efficient behaviour. Most of the FGs’ participants reported to be unsure if information and communication campaigns could lead them, or the others, to adopt more energy efficient behaviour: “Woman(W)1: Campaigns are useful but insufficient, (to promote behavioural change), …W1: and they won’t manage to reach everybody…W2, (complementing the idea from W1): people hold strong ideas, I always did things this way why should I change now, (discussing the adoption of more energy efficient behaviours)” FG7 “W1: we see a campaign providing information on how we could save…W2 it’s only an advertisement…W3: we don’t pay much attention…W1: one reads but doesn’t memorize…W2: we do nothing, unless we are touched for some reason like the recycling campaigns or those campaigns to feed people in need…those messages have an impact” FG6 Findings thus indicate that information and communication campaigns could be effective in encouraging the adoption of more energy efficient behaviour, but that this encouragement alone might not be sufficient due to a basic lack of motivation to adopt more energy efficient behaviour. During the FGs, participants were asked to design an information and communication campaign that could be implemented nationwide in order to promote the adoption of more energy efficient behaviour. The issues discussed during the design process were wide ranging and highlighted the complexity of promoting the adoption of more energy efficient behaviour, with a number of desirable characteristics of future communication and information campaigns emerging. Among these, FGs’ participants focused on the need to provide information regarding the contribution for specific individual home appliances and associated practices, as well as how much could be saved by adoption different behaviours. This shows that FGs’ participants attributed a high level of relevance to understanding how much energy specific home
  • 202. 8. Intervention strategies and perceived effectiveness 182 appliances consume and how energy is used within day-to-day practices, in order to consider to adopt more energy efficient ones. This is well in line with the discussion in section 8.4.1 and provides further evidence that FGs’ participants and CID interviewees lack information regarding energy used under specific circumstances and as a consequence, of how much energy could be saved. Also, FGs’ participants focused on providing positive messages that could enhance the ‘fun’ part of saving energy, rather than on the perceived obligation of doing so. “To have a ghost that went behind and switched lights off” Female, FG7 “I don’t think there is the need for recrimination…I believe that to recriminate introduces a negative dimension that I don’t find essential for changing behaviours…the child can suggest to the mother and the mother can answer that you are right, I was not even recognizing what I was doing, (discussion during the design of the communication campaign), Female, FG2 Positive messages were perceived as stressing the results of saving behaviour, which might be a reason for all suggested campaigns to have very similar slogans, focusing on the idea of saving, on short term- immediate change, and highlighting the financial impact of saving. These findings highlight FGs’ participants focus on short-term, immediate gains rather than long-term investments in energy efficiency, which, in general, is opposite to the majority of campaigns that focus on long-term gains, as well as more abstract terms of saving the environment, or saving the planet. A more recent communication campaign in Portugal has been stressing the immediate gain, in particular the cost-saving potential day-to-day, that energy efficient behaviour can have. Only a few FGs’ participants agreed to the use of shock, fear, or blame messages to promote more energy efficient lifestyles. These messages were, for the majority of the FGs’ participants, perceived as not contributing to the success of the campaign and FGs’ participants used the example of cigarette packets with warning messages and images and how smokers found a way to avoid these by buying a cover for the packet. Analogous to positive, fun messaging, the opposite, fear and blame messaging, were perceived as not leading to individual identification, as there seemed to be a related fatigue and tiredness regarding negative messages that could enhance a feeling of helplessness and guiltiness and as a consequence, of disempowerment:
  • 203. 8. Intervention strategies and perceived effectiveness 183 “Nowadays we are addressed each day with negative things…it’s too much” Female, FG7 “I would become very frustrated since I already save in so many things, with more energy efficient light bulbs and whatsoever, that I believe I have the right of having a longer shower” Female, FG6 Overall, findings from the FGs suggest that communication and information campaigns can be used as a way to provide information and to generally highlight the benefits of adopting more energy efficient behaviour. Findings indicate further, that information campaigns might not necessarily lead to action since there might be a lack of motivation to adopting more energy efficient behaviour. As such, findings from this research do support the literature in that communication and information campaigns might have little, or no, impact on promoting individual behavioural change and thus can be expensive in relation to their effectiveness, (Southerton et al., 2011; McKenzie-Mohr 2000). 8.3.3 Education interventions During the FGs, the provision of formal education emerged as one of the interventions that could encourage the adoption of more energy efficient behaviour by current, as well as future generations. A number of FGs’ participants acknowledged that during their school education there were not that many educative programmes that provided them with an understanding of the environmental impact of their behaviour. “My son went to the kindergarten and teachers focus a lot on the environment, not on the use of water or electricity but rather in terms of recycling and the environment” Female, FG6 However, they noticed that nowadays, children at school learn how to behave in a more environmentally friendly way, providing the example of recycling as one such intervention area. As a result of this school effort, FGs’ participants agreed overall that this could have a positive impact on their children’s future behaviour, which potentially could be more energy efficient and environmental friendly and simultaneously have a side effect on the parents’ behaviours as a result of child influence and pressure. Yet, simultaneously, this is also an example of how FGs’ participants do not perceive themselves as being
  • 204. 8. Intervention strategies and perceived effectiveness 184 responsible for their current behaviour in terms of energy use at home. During the FGs, a number of participants referred to the pressure they felt from their children to recycle at home and how this has become ingrained into the family routine. Yet, in the case of energy, such pressure could not be clearly identified. Nevertheless, this might also be related to the fact that recycling education efforts have a long tradition within the Portuguese school system, as opposed to the energy-focused interventions that are more recent. 8.3.4 Community based interventions Findings from this research suggest FGs’ participants and CID/PID interviewees value their ability to provide their families with comfort and wellbeing levels that are, socially, perceived as required and desirable to have, regardless of the amount of energy that is required to supply these. During the FGs and CID/PIDs, participants and interviewees often compared their energy use to those of family members, friends, or people having a house with similar characteristics. This was perceived as sufficient to justify their energy use at home as normal, or average, even if it included non-essential, but rather desirable needs. Shared practices that are perceived as part of this normal energy use include owing several TV sets, having more than one shower per day, or leaving home appliances on stand-by mode; with the first two representing a normal comfort level and the last the convenience of less energy efficient behaviour. The understanding of normal energy use as a comparison has been discussed in chapters 6 and 7 and further explored within a reward-penalty system in section 8.2.1. By calculating the base energy use level, household energy use can be compared against other households and would allow identification of those households that have average consumption and those that over-consume or under-consume energy at home. Nevertheless, only one of the PID interviewees, (PID3), was in favour of such an approach since it was considered to appeal to a competitive nature and would influence, what he understood as an, individual’s unwillingness to lose at a game. “I guess those examples you provided, to measure, to use inexpensive monitoring equipment to reach the consumer, to guide the consumer in real time. The truth is not for those in energy poverty, but for the others this is small money when compared to a restaurant bill or a cinema
  • 205. 8. Intervention strategies and perceived effectiveness 185 ticket. People will save more by enrolling in a game, that will stimulate their competitive behavior, no one likes to lose a game”, PID3 Ultimately, it appeard as if the relative and comparative aspect of energy use did support building up an understanding of what is understood as being a normal consumption, which in the case of relative over- spending would thus be a questionable incentive to use less energy, in combination with feedback provision and monitoring equipment, (see 8.4.3). Nevertheless, the results from this research are not conclusive regarding the effectiveness of how such a comparison system would encourage the adoption of more energy efficient behaviour. But, to provide feedback on energy use, based on a comparison system, could be an alternative to complement the provision of individual feedback regarding energy use and improvement in the effectiveness of interventions. As such, collective feedback strategies that use neighbourhood data to feed comparitive use data, may be a useful addition to individual household feedback as an intervention strategy, that encourages the adoption of more energy efficicent behaviours. 8.4 Combined structural/psychological interventions This section provides an overview on aspects that have been discussed within the FGs from both, a structural and psychological intervention perspective that are, thus, presented in this section, providing a combined look at structural and psychological intervention. 8.4.1 Information, feedback and monitoring equipment There was an overall agreement among FGs’ participants and PID interviewees regarding the role that monitoring equipment could have as a way of, “Commoditizing”, behaviour into a good proxy, in order to make consumption visible, as suggested by WWF (2008). FGs’ participants and PID interviewees suggested the use of monitoring systems, such as energy meters, as one suitable option of providing continuous feedback about the amount of energy being used. During PID, interviewees acknowledged the difficulty that energy invisibility could add to the aim of promoting the adoption of more energy efficient behaviour, as well as the role that monitoring equipment could have in terms of providing some visibility to home energy use, as the following quote demonstrates:
  • 206. 8. Intervention strategies and perceived effectiveness 186 “One of the most important aspects for changing energy use is its visibility. During the 'ecofamílias' 17 project with the use of energy meters…we managed to materialize energy, something that otherwise is invisible and we did it fairly successfully”, PID1 Though only a few FGs’ participants had experience with energy meters, the majority of FGs’ participants agreed that in order to be effective, such type of monitoring equipment must provide simple information. During the FGs some examples of what was meant by simple information were provided, such as a simple colour system indicating whether consumption was within a certain range, or simple alerts triggered once reaching a defined value, with the information supplied in Euros and other units, such as kW or CO2, an add- on that could be provided if wanted. This same opinion was shared among PID interviewees, who agreed that provided information should be simple, in order to be useful and support individual decision-making. If these conditions were met, energy meters, or similar monitoring equipment, were perceived as holding a potential to promote more energy efficient behaviour and thus for energy to be saved. However, this almost unanimous, opinion regarding the use of energy meters, or similar monitoring equipment, might need to be evaluated with care, since when questioned about the effectiveness of providing real time information and how this could influence the adoption of more energy efficient behaviours, three alternative opinions emerged among FGs’ participants: (1), those FGs’ participants that were convinced of the benefits of knowing their detailed energy use, as this would lead to the adoption of more energy efficient behaviours; (2), those that recognized that holding this level of feedback would be of interest to them, though it would not have an impact in terms of the adoption of more energy efficient behaviours; and (3), those that were not interested at all in learning about their energy use, since this could cause feelings of frustration and disappointment: “But it is only a soup I’m warming up” (note: when discussing the impact of knowing how much energy was spent for warming up a soup at the microwave and whether this could influence her individual behaviour, which was perceived as severely conditioned by her financial situation already), Female, FG7 17 Ecofamílias project had 3 editions and involved a total of 1.225 families with the aim of evaluating their ability to reduce their energy use at home.
  • 207. 8. Intervention strategies and perceived effectiveness 187 This diversity of opinion thus questions the effectiveness of providing real time feedback; whether monitoring equipment could promote long-term adoption of more energy efficient behaviours, or whether this would rather be a short-term phenomenon. Though FGs’ participants acknowledged the potential of monitoring systems to allow them to improve their knowledge regarding the contribution of specific energy related behaviours to their monthly bill, even those FGs’ participants in favour of having a monitoring system at home shared the opinion, that, with time, they might lose interest in constantly monitoring their energy use. For this reason monitoring equipment might only have a short-medium term impact: “I have no idea how the monitoring equipment would be but if I would need to check for the energy being used each time, I used x amount of energy, I used x amount of energy, I believe I would get upset after a while”, Female, FG7 The potential effectiveness of the use of monitoring equipment in combination with prompting strategies will be further discussed in the subsequent section. 8.4.2 Smart metering and prompting strategies Prompting strategies appeared to be less known, though ultimately, FGs’ participants provided several examples. One FGs’ participant used post-it notes to remind family members on what they should do, another one referred to a mobile phone that produces a noise once charged, or another referred to home appliances that produced some kind of sound as a reminder that they are still in standby mode. Overall, the inclusion of integrated smart features into home appliances appeared to be very well accepted by the majority of the FGs’ participants, which could provide opportunities to effectively prompt individual behaviour, with the message being displayed in close proximity to the place where the target behaviour can be performed, as, for example, suggested by Geller et al., (1982), three decades ago. These smart features were perceived by FGs’ participants as having a prompting role in reminding users to adopt more energy efficient behaviour in order to reduce energy use. Findings, thus, suggest that prompting strategies could be the counterpart to the barrier of, “I forgot doing so” and fall in line with literature claims (see section 4.5.1.) that smart features hold great potential due to their proximity to where the action takes place. Findings thus support earlier studies that suggest smart features could be a, relatively, low cost type of intervention,
  • 208. 8. Intervention strategies and perceived effectiveness 188 to promote the adoption of more energy efficient behaviours, (Lehman & Geller, 2004). Yet, FGs’ participants felt overall that these prompts should be stated positively, to avoid eliciting negative reactions, (see also 8.3.2) and that they should be labelled to provide information designed to help consumers make informed choices, (see also 8.2.3). 8.4.3 Information, feedback and energy bills According to the findings in this research, energy bills might not be the most efficient strategy to provide people with information on how much energy they have used, or at least not for the case of Portugal. The majority of FGs’ participants found it difficult to understand how much energy they used during a specific month for a number of reasons: in Portugal energy bills include other fees and surcharges not related to the amount of energy being consumed, often they are bi-monthly, (each covering two months) and based on an estimated annual consumption, or fixed for 11 months. As a result of this, FGs’ participants reported difficulty in understanding the amount of energy used for a specific month, as well as what might have contributed to a differing energy use per month. Only a few FGs’ participants appeared to be well informed about their actual monthly energy use and were quite happy and willing to share the data. FGs’ participants suggested that in order to be more useful, energy bills should provide information in an easily understood way, such as a bar graph with monthly consumption based on real consumption, or a comparison in a way they could relate to, such a basic home appliance. Overall findings from FGs are well in-line with the literature, (Brandon & Lewis, 1999; Darby, 2006) and provide further evidence on the role, but also the limitations for energy bills to provide useful feedback on energy use. 8.5 Concluding remarks This chapter discusses the findings from the empirical study looking at the potential effectiveness different intervention strategies to encourage the adoption of more energy efficient behaviours at home within the Portuguese context.
  • 209. 8. Intervention strategies and perceived effectiveness 189 In the following table the findings from the research presented in this chapter are related to RQ3, highlighting including any noteworthy deviation from the reviewed literature that could be detected from the findings of this research .
  • 210. 8. Intervention strategies and perceived effectiveness 190 Empirical study findings RQ Noteworthy further observations Chapter Section: 8.1. Communication Design Persuading people to adopt more energy efficient behaviour, generally seen as challenging for less, ‘easy and simple’, behavioural changes, or once not having an impact on desired normal levels of comfort, convenience or wellbeing. RQ3b People do not appear to hold any inconsistency between their attitudes and their behaviour, if one considers that their positive attitudes towards comfort and wellbeing are stronger than their attitude towards the environment. RQ3a Previous messages from interventions do not appear to be aligned with those behaviours that people accept doing, but rather to the ones they reject, or are not committed to doing. RQ3a Chapter Section: 8.2. Structural interventions 8.2.1. Rewards and punishments Findings suggest that a rewards/punishment system might be effective for some people to encourage the adoption of more energy efficient behaviour. RQ3a, RQ3b The potential effectiveness of rewards/punishment system could not be fully understood, in particular to the medium/long term. 8.2.2. Provision of incentives and samples Findings suggest the provision of incentives and samples could encourage the introduction of more energy efficient technologies by reducing the investment required and risk of such a purchase. RQ3a
  • 211. 8. Intervention strategies and perceived effectiveness 191 Empirical study findings RQ Noteworthy further observations 8.2.3. Labelling The efficacy of labelling could not be fully understood, as people might lack the ability to fully understand the information provided. RQ3b ‘A rated’ seen as synonym for energy efficient, without considering actual use. Observed lack of ability across all FGs to understand energy labels, to use them as a means to actually compare the performance of home appliances, resulting in an apparent lack of effectiveness of such labels. 8.2.4. Demonstrating and facilitating as an intervention strategy Modelling behaviour was seen as a potentially effective avenue for changing behaviour, as people will follow these examples once they are understandable, relevant, meaningful and rewarding, in terms of positive results. RQ3a, RQ3b 8.2.5. Environmental design and material contextual adjustment Even though the contribution of technology could play an important role, there is some common agreement that technological solutions to domestic energy reduction might be insufficient without the cooperation of individuals. RQ3a Apparent neglecting of interventions aimed at how the home and home appliances are used and how they can be adjusted on an everyday base. Product design and contextual adjustments could be effective, but will not necessarily encourage the adoption of more energy efficient behaviour, being a more technofix approach.
  • 212. 8. Intervention strategies and perceived effectiveness 192 Empirical study findings RQ Noteworthy further observations Chapter Section: 8.3. Psychological interventions 8.3.1. Targeted face-to-face information and feedback Face-to-face information appears to be the desirable alternative to received customized information, yet it might not lead to the adoption of more energy efficient behaviour. RQ3a Information should be provided first in monetary terms, and potentially also in other units such as CO2. Overall concern regarding which information is correct and whom can people trust. 8.3.2. Information and communication campaigns Information and communication campaigns are perceived as an adequate alternative to provide information and raising awareness, but might have little or no impact on encouraging behavioural change. RQ3a, RQ3b Low incidence of recall for energy saving campaigns Encouragement via information and communication alone might not be sufficient to lead to change due to a basic lack of motivation to adopt more energy efficient behaviour. FGs’ participants focused on providing positive messages that could enhance the fun part of saving energy rather than on the perceive obligation of doing so. 8.3.3. Education interventions The provision of education is perceived as an effective strategy to encourage the adoption of more energy efficient behaviour by todays’ and future generation. RQ3a, RQ3b Recycling as an example for perceived success of behavioural change interventions in Portugal. Recycling as an example for children pressuring parents to recycle at home and how this became ingrained into the family routine. 8.3.4. Community based interventions Comparing individual energy use to that of other community members could be an effective means of information provision, that could provoke and encourage the adoption of more energy efficient behaviour by providing comparative feedback, a feeling of competition, social comparison, or social pressure. RQ3a, RQ3b Collective feedback strategies that use neighbourhood data to feed comparative use data, may be a useful addition to individual household feedback as interventions that encourage a change in energy behaviour.
  • 213. 8. Intervention strategies and perceived effectiveness 193 Empirical study findings RQ Noteworthy further observations Chapter Section: 8.4. Structural/Psychological interventions 8.4.1. Information, feedback and monitoring equipment Information should be provided firstly in monetary terms, and potentially also in other units, such as CO2. RQ3a The use of energy meters, in terms of acceptance and impact level, apparently do vary, ranging between appreciation to annoyance. 8.4.2. Smart metering and prompting strategies Prompts could be an effective intervention to remember easy to do activities. RQ3a FGs’ participants overall felt these prompts should be stated politely to avoid eliciting negative reactions, (see also 8.3.2) and that they should be labelled in such a way as to provide information designed to help consumers make informed choices, (see also 8.2.3). Smart features could be a, relatively, low cost type of intervention to promote the adoption of more energy efficient behaviour. RQ3a Integrated smart features could provide a set of opportunities to effectively prompt individual behaviour, with the message being displayed in close proximity to the place where the target behaviour can be performed. 8.4.3. Information, feedback and energy bills RQ3b Energy bills might not be the most efficient strategy to provide people with information on how much energy they have used. Table 8-1 – Summary of findings relating to RQ3
  • 214. 8. Intervention strategies, behavioural change and energy efficiency 194 Here, a summary is provided on how the results reported in this chapter provide answers towards research questions 3, (RQ3), “What is the potential role of intervention strategies on energy use at home” and the sub-questions, “What are perceived requirements of intervention strategies”, (RQ3a) and “What are individual perceptions on the effectiveness of intervention strategies”, (RQ3b). With regards to the perceived requirements of intervention strategies, findings presented in section 8.1 highlight how important it is to send the appropriate message by the appropriate messenger, so that the target audience identifies with the message and increases the likelihood of them acting as desired. As can be seen across sections 8.1 to 8.4, persuading people to adopt more energy efficient behaviour appears to be challenging and, in particular, for less ‘easy and simple’ behavioural changes, or those perceived as impacting desired ‘normal’ levels of comfort, or wellbeing. As shown through the chapter the provision of information and feedback, in its various forms, had been perceived as being efficient in providing information and raising awareness towards more energy efficient behaviour. Yet, once it came to individual experience and actions, it equally could be seen that FGs’ participants did often appear to lack of motivation. In this regard it was not possible to understand how these perceived requirements, for interventions to be successful, could address the observed lack of motivation for adopting more energy efficient behaviour, and that they frequently appeared to be anchored on the motivation to provide their family with socially agreed normal levels of comfort and wellbeing. With this, the overall efficacy of interventions might be questioned. These findings, do however, support earlier findings that information and feedback provision alone might not be sufficient to effectively encourage the adoption of more energy efficient behaviour and thus might require information and feedback provisioning to be used, in combination with other type of interventions, so to increase their chance of success, as suggested, for example, by Abrahamse et al. (2005), or Southerton et al. (2011). During the empirical study, an example of such a combination emerged and was related to the need for information and feedback to be used in combination with promoting the adoption of a social understanding of normal energy use. As such information provision might not be a panacea for the effective adoption of more energy efficient behaviours. As could be seen through chapter eight, contextual intervention strategies that were perceived as more efficient included, the adjustments within product design, house infrastructures and home appliances and all, to a certain degree, removed the responsibility from the user to adopt more energy
  • 215. 8. Intervention strategies, behavioural change and energy efficiency 195 efficient behaviour,(Southerton et al., 2011). An additional focus, thus might be placed on providing effective incentives and punishments, in combination with a community level type of intervention drawn on comparative feedback, instead of the individual approach that appears to have dominated so far, as suggested by Abrahamse et al. (2005), Darby (2006), EEA (2013), Heiskanen et al. (2009), or Middlemiss (2008).
  • 216. 9. Conclusion 196 9 Conclusion This study investigated domestic energy use behaviours in the Portuguese context and aimed to explore how the adoption of more energy efficient behaviours at home could be encouraged. With this the research has three objectives. First it attempts to provide an overview of what explains and influences energy use at home (RQ1). Second it has the objective to advance on the theory of motivating, enabling and reinforcing factors that could promote the adoption of more energy efficient habitual behaviours and practices at a household level (RQ2). Thirdly, this research has the objective to explore the potential effectiveness of change interventions within the field of energy use at home and the different types of interventions that might be used (RQ3). 9.1 Specific answers to the research questions 9.1.1 RQ1: What explains energy use at home? As has been shown throughout the research, energy use is not the result of a single determinant, but rather the result from a number of internal and external determinants. The determinants and existing conditions found through this research, appear to be in overall support of the literature presented in chapter 2 and, notably, with the works of BPIE (2011), DGGE/IP-3E (2004), Goldblatt (2005) and Maréchal (2010). With regards to home appliances, this research provides further evidence that the ever-increasing number of home appliances does increase energy use, (6.2.1; 6.2.3). But, this simultaneously helps to trigger participants’ awareness of the need to purchase more energy efficient appliances so to reduce energy use, (6.2.4). As could be seen in both, the empirical work and the literature, participants not only substituted old, obsolete home appliances, but also bought more appliances overall (2.2.). Throughout this research, the availability of energy was never truly questioned by the participants, with energy being perceived as something essential for people to live in the way we, in an industrialised nation’s context, have become used to, (6.1.2). With this, it could also be seen that energy is an intermediary between need and fulfilment of need, as part of a socio-economical-techno-cultural combination that frame ‘our’ needs, opportunities, belief systems and abilities, (7.1; 7.2.3). Findings from the empirical study did
  • 217. 9. Conclusion 197 show the relation between ‘energy prices & energy use’, as well as ‘disposable income & energy use’, with both constituting determinants for energy use, (6.2.4). Though saving money seemed not to be a main priority for the adoption of more energy efficient behaviour, but rather to maintain existing behaviour as long as deemed affordable, (7.1.1). Findings from the FGs and interviews reveal a tendency for higher reported income levels to be associated with higher, reported, energy use, with participants agreeing that perceived ‘needs’ increase with income level, (6.2.5; 6.2.6.), which appeared aspired to by those on lower incomes, (6.2.5.). This assumption is supported by earlier research, (WWF, 2012; DECC, 2011; Gatersleben et al., 2002; 2.2; 2.2.5.; 2.2.8). Findings from this research indicate that the majority of the participants will maintain their behaviour, even if prices increased, as long as they could afford doing so, (6.2.4), thus providing further evidence to the body of literature regarding energy use as price inelastic in the short term, (DECC, 2011; Gatersleben et al., 2002, Sorell, 2007; 2.2.4; 2.2.5; 2.2.8.). However, considering that overall energy consumption declined in Portugal as a result of the economic crisis (1.7) this also suggests that some people stopped being able to afford their former energy level. More precisely it could be observed, (6.2.4; 7.1.1), that energy and fuel poverty seem to be a reality for a number of people within the empirical study, with participants not being able to guarantee services such as heating their homes, or to afford to spend more of their monthly income on energy. For the case of Portugal it also could be seen that poor building envelopes and infrastructures (2.2.7) could further impact upon energy and fuel poverty. In any of such cases people are forced to use less energy if prices rise, which has also been found in other studies, (Boardman, 2010; Buzar, 2007a; Healy, 2003; SEI, 2003; SILC, 2007; WHO, 2012; 2.2; 2.2.5.). This research further shows that existing habits are a driving force for energy use and represent a challenge to the effective adoption of more energy efficient behaviour, since most energy related behaviour are of a habitual nature and often acquired over time, (7.3.1), supporting existing studies, (IPPR, 2009; Green Alliance, 2011, Jackson, 2005; 3.4.1). 9.1.2 RQ2: What influences energy use at home? As could be seen, barriers appear to influence energy use more than motivations and outnumbered motivations in each of the three phases of the research; even existing motivations ultimately did not appear to result in any actual energy usage reduction, (7.1; 7.2; 7.3). Motivational variables appear to be in direct
  • 218. 9. Conclusion 198 competition with barriers and findings indicate that the reported barriers are, perhaps, not actual barriers, but in part a convenient excuse, (7.3.4.). Therefore, energy use is perhaps less influenced by ‘being able’ to adopt more energy efficient behaviour and more about ‘being willing’ of doing so. As such, findings do support the literature that people tend to say that they cannot perform the behaviour, (low self-efficacy), rather than they will not perform it and, in particular, once they anticipate an aversive outcome, such as reduced level of comfort, they are no longer willing to adopt behaviour that may produce such an outcome, (Allen and Ferrand 1999; Baker & Kirsch, 1991; Bandura, 1986; DECC, 2011; EEA, 2013; Jackson, 2005; Kollmuss & Agyeman, 2002; Leiserowitz et al., 2011a; Prendergrast et al., 2008; Shove, 2003; Vandenbergh et al., 2008; 3.4.2; 3.4.4). This could help explain why energy use has not been decreasing more notably in Portugal despite the growing number of governmental supported tangible and intangible interventions (1.7). This is also supported through the apparent observed importance and role, of norms, habits and beliefs with regards to lack of efficacy, or the understanding of giving up something, that were frequently highlighted as main barriers towards the adoption of more energy efficient behaviour by the participants of this research, (7.2.3; 7.3.1; 7.3.3). Findings further reveal that attitudes and values might influence energy use at home once it comes to family comfort and wellbeing, with values, attitudes and behaviours being well aligned and resulting in a potentially higher energy use at home, (7.1.2; 7.3.2; 8.1). Furthermore, there seemed to be an individual resistance towards specific behaviours that did compete with wellbeing, convenience and comfort, (7.1.3; 7.3.2; 7.3.4), as has also been found in other studies, (DECC, 2011; EEA, 2013; Jackson, 2005; Prendergrast et al., 2008; Shove, 2003; 2.2.2; 2.2.5; 3.3.1; 3.3.3; 3.4.2; 3.4.4). Participants appeared to be quite comfortable with a, certain, level of normal energy use and there appeared to be a socially shared understanding of this normal that directly seemed to influence energy use, (7.3.2), as is also known from the literature, (Goldblatt, 2005; Maréchal, 2010; Shove, 2004; 2.2.1; 2.2.3). Further to this, existing energy use habits were reported as highly influencing energy use, due to the difficulty of challenging and changing such habits and encouraging more energy efficient ones, (7.3.1). In addition to this, findings from this research, (6.2.4; 7.1.1; 7.3.2), support the literature, (DECC, 2011; Gatersleben et al., 2002; 2.2; 2.2.5; 2.2.8), that a higher income level might be associated to higher energy use. Those who are more affluent appear willing to trade money for what they see as normal comfort and
  • 219. 9. Conclusion 199 convenience, giving priority to individual and family wellbeing, rather than for environmental protection. Nevertheless, this might not be a conscious, “trade off”, between energy costs in relation to income, but rather that energy seems to be cheap to some of the participants and thus there is no rationale to consider reducing usage. A longer-term view, regarding environmental protection, might be required to build a response to this sort of rational. In contrast to this, those in energy and fuel poverty appear to not be able to reach the aspired normal comfort level, suggesting that an increase in income could promote higher levels of energy use at home, (6.2.5.). This research provided evidence that the amount of those in fuel poverty might be higher than what is commonly perceived and much in-line with the existing statistics and assumptions from literature, (Healy, 2003; SEI, 2003; SILC, 2007; WHO, 2012). With regards to these factors that seem not to influence energy use at home, findings from this research, (7.1.2; 8.1), suggest that pro-environmental values and attitudes are among the determinants that appear to have less influence on the amount of energy being used at home. This supports the findings from earlier studies, (Kollmuss & Agyeman, 2002; McKenzie-Mohr & Smith, 1999; Poortinga et al., 2004; Schultz et al., 1995; Thøgersen, 2004; 3.2). 9.1.3 RQ3: What is the potential role of intervention strategies on energy use at home? Findings from this research suggest that any attempt to reduce energy use at home would face strong competition from the, perceived, normal level of use, (9.2.1). To support the adoption of more energy efficient behaviour at home, intervention strategies must change this understanding of normal to a clearly defined new level that is considered sustainable and desired, (8.1). During this research it was, however, not possible to understand how existing norms could be effectively integrated within future interventions, (6.2.5; 7.2.3; 8.2.1). As such, little evidence was uncovered during the empirical study to suggest that norms could be used to encourage the adoption of more energy efficient behaviour, (6.2.5), as suggested by the literature, (section 2.2.3). Other strategies to interventions that might be adopted include choice architecture, product design, or penalty-incentive approaches, as they circumvent decision-making based on shared understandings of comfort, wellbeing and individual preference, (8.2.1; 8.2.5). However, the literature suggests that such
  • 220. 9. Conclusion 200 strategies would, in addition, need to pay attention to, ‘intrinsic motivation’ and cultural and infrastructural influences, (Dwyer et al., 1993; Lutzenhiser, 1993; Lowe, 1996; Wilhite and Shove, 1998; 2.2.). Since a focus on ‘knowledge-penalty-incentive-behaviour’ might fail to recognise the complexity and dynamics in which energy use is embedded in the flow of day-to-day life. Thus, the ultimate suitability of choice architecture, product design, or penalty-incentive strategies, perhaps, would need to be further examined in light of the existing literature. Findings equally show that the evaluation of previous attempts might also impact the potential effectiveness of interventions. Thus, in planning intervention strategies it might be required to consider the outcome expectations people have, regarding the efficacy of individually adopting more energy efficient behaviour, as well as to collectively engage in them, (7.3.3; 7.3.4). As has also been suggested in the literature, (Bandura, 1977a; Cialdini et al., 1990; Martiskainen, 2007; van der Pligt, 1985; 3.3.3; 3.4.3). All of these findings also show that frameworks that attempt to support intervention strategies must provide the right interplay between the various existing factors and as further discussed in section 9.2. 9.2 Key findings This section provides an overview of the key results of this research and the contribution it makes to the field of knowledge in sustainable energy use. A particular focus is on how the adoption of more energy efficient behaviours at home could be encouraged, in the context of understanding existing determinants, motivating, enabling and reinforcing factors and the related implications towards intervention strategies. The findings of this research generally show that if the rate of adoption of more energy efficient behaviour is to increase, then interventions that are focusing on providing information or financial incentives are unlikely to work for a large proportion of energy users. Instead, the adoption of more energy efficient behaviour at home depends on the ability of intervention strategies to challenge existing norms, thus creating new understandings, expectations and utilization of energy services that could manifest in the adoption of more energy efficient behaviour. As such the work has shown that community-based initiatives might be an adequate means to challenge social norms and to bring about change and as detailed in following sections.
  • 221. 9. Conclusion 201 9.2.1 Importance to challenge the understanding of normal Section 4.1 discussed a number of frameworks that could support intervention strategies and that attempt to provide the right interplay between the various existing factors. And indeed the findings from this research do support the impact that the various external, internal or social factors, such as norms or habits, could have. With this findings do support earlier studies that (Prendergrast et al., 2008) informational and financial levers alone might not be sufficient to promote individual behavioural change, but instead would require frameworks that attempt to change existing perceptions, knowledge, attitudes, norms and values (Abrahamse et al., 2005), or that go beyond the individual and also address the community level and the social aspects of energy-related behaviour (Abrahamse et al., 2005; Darby, 2006; Heiskanen et al., 2009; Middlemiss, 2008). With this the findings of this research do suggest that the frameworks and models presented in sections 4.1 and 4.2 indeed could support intervention strategies to find the right interplay. A common finding across all of the three empirical phases of the research had been the unwillingness to adopt more energy efficient behaviour, mainly for the reason that they are perceived as impacting established levels of comfort, convenience and wellbeing, (6.2.5; 7.3.2; 7.3.4). This unwillingness appeared to relate to what is perceived, expected and socially accepted as normal energy use, normal comfort levels, normal services that energy provides, that have entered peoples’ day-to-day lives, (7.1.3; 7.3.2). Expectations of energy services and use are normalised in terms of levels of comfort and to challenge that, in asking people to adopt different behaviour, challenges the core expectations that have become established, (7.2.3; 8.1). From such a perspective, the adoption of more energy efficient behaviour at home depends on the ability of intervention strategies to challenge the existing norm, so to create a new understanding and expectation of energy services that could become manifest in the adoption of more energy efficient behaviour, (7.2.3; 8.1). As can further be seen, the ability of intervention strategies to provide opportunity to understand and compare one’s energy use and to provide customized circles of information and feedback, (7.2.2; 8.3.1; 8.3.4; 8.4.1; 8.4.2), or, to question and promote debate, with regards to normal and taken-for-granted practices, (7.3.2), appear to hold high potential to increase the likelihood of success of intervention strategies.
  • 222. 9. Conclusion 202 9.2.2 Invisibility of energy and its implications Previous research, (Burgess & Nye, 2008; Darby, 2006; Hargreaves, 2012; 2.2.), suggests that ‘invisibility’ is a distinctive characteristic of energy use at home and this study supports this, with participants considering energy as intangible and abstract when compared to other utilities, (6.1.1.). Participants compared the energy that flows in pipes inside the home to the water they see flowing out of the tap and energy invisibility, indeed, appeared to be a distinctive characteristic of energy, when compared to other utilities, (6.1.1.). Despite being a distinct characteristic, the empirical study did however equally provide some evidence, (6.1.1.), that increasing energy visibility perhaps does not result in the adoption of more energy efficient behaviour. Findings from this research show that invisibility did constitute a barrier for the adoption of energy efficient behaviour, (6.1.1.). What remained to some extent unclear through this work is what impact, ultimately, would an increase in visibility have in terms of energy use. The findings obtained are in support of the literature, (Abrahamse et al., 2005; Geller, 2002; Martiskainen, 2007; Staats, Wit, & Midden, 1996; 2.2.1; 2.2), that even if energy use becomes visible, the impact of this visibility on energy use and on the adoption of more energy efficient behaviour might be limited, (6.1.1). 9.2.3 Financial motivations to save energy During the empirical study saving money, or reducing cost, appeared to be the main motivation for individuals’ to save energy, (7.1.1; 7.1.2). However, findings from this research equally indicate that this motivation directly competes with motivations of not reducing energy use, such as to maintain existing comfort levels, (7.3.2). Moreover, participants in this research appear to be aware of this competing situation and preference for increased energy use, appearing to feel comfortable with this as long as they could afford it, (6.2.4; 7.1.1.). Further evidence was found that energy use is mostly the result of a focus on the services that energy provides, (6.1.1), such as cooking, lighting, or enjoying a movie, rather than considering the energy being used, (Goldblatt, 2005; Martiskainen, 2007; 2.2). This might be in particular problematic as the number of home appliances owned is constantly increasing, as are the related practices to such appliances, such as heating or cooling homes, (6.2.1; 6.2.3). Within this work it was, however, not possible to clearly understand the scope of association between ‘practice’, ‘services’ and ‘energy use’, nor whether this could influence the purchase decision towards more energy efficient home appliances, (6.2.4).
  • 223. 9. Conclusion 203 Thus, despite being reported as the most important motivating factor for saving energy, the findings from this work rather suggest that financial motivations appear to not be a main priority for adopting more energy efficient behaviour, (7.1.1). An exception to this are those people on a low income that find themselves in a situation of energy and fuel poverty, to whom reducing energy bills, thus saving money, would be crucial, (6.2.4; 7.1.1.). This study provided further evidence the amount of people that live in a situation of energy or fuel poverty might be higher and what is commonly perceived in a Southern country. 9.2.4 Knowledge, competence and self-efficacy Findings from this research indicate that participants do hold a good level of information regarding energy efficient behaviour; with this level of information decreasing once it impacts specific behaviours. This suggests the need for improving the householders’ knowledge on the specific behaviours they could adopt and customizes to their reality and needs, as opposed to general information, (7.2.2). In addition to this, most of the more energy efficient behaviour appears to have been learned during childhood and through life experience, rather than as a result of information received through any type of intervention, (7.3.1; 8.3.3). The findings also show that to encourage the adoption of more energy efficient behaviour might thus also require increasing knowledge, competence and self-efficacy and not simply provision of information through, for example, the design of customized utility bills, (8.4.2), the provision of energy labels, (8.2.3), the provision of energy meters, (8.4.1), or of tariff structure adoption, (8.2.1). As can be seen from both this work, (7.2.2; 8.1; 8.2.3; 8.3.1; 8.3.2; 8.4) and the literature, (3.1; 3.2; 3.3; 3.4; 4.2; 4.4; 4.5.), strategies of information-based interventions may not be enough to effectively challenge expectations of energy needs and encourage people to adopt more energy efficient behaviour. 9.2.5 Energy efficient behaviour and outcome efficacy Participants in this research declared an, apparent, overall preference for ‘easy to do’ energy efficient behaviours, e.g. switching lights off when not in use, that frequently appeared to result in a belief of having done their bit, or even everything they could, to save energy, which have also been an often-reported reason for not adopting additional energy efficient behaviour, (6.2.1; 7.3.3; 8.1). This understanding of doing ‘their bit’ appeared to be often associated with a lack of perceived collective efficacy, be it within the
  • 224. 9. Conclusion 204 family setting, among their family and friends, or even society, (7.3.4), and much in support of the work of Cialdini et al. (1990) and van der Pligt (1985) and as discussed in 4.2. This is to say that participants from the empirical study often reported they felt that they were alone in their efforts and not supported by family, friends or society, to adopt more energy efficiency behaviour. This negatively impacted their perception of the efficacy of their efforts and their outcome efficacy. 9.3 Limitations of the research This research has a number of identified limitations. First of all, it cannot claim to be representative for the Portuguese population. Even though the quantitative survey used representative sampling, the focus groups were only conducted in two different locations in the North of Portugal and consequently, do not necessarily provide a representative view of the Portuguese population. The fact that both the sample of participants in FGs and CID interviews was limited to a range of consumers who shared a geographical location, which might have limited the diversity of answers. A second limitation is that the study measured self-reported intentions and willingness to act; but not actual behaviour. Responses might, thus, not be as accurate as they could have been, due to, for example, influence by social desirability, or other self-report distortions, (such as recalling difficulties), as is known from the literature, (e.g. Darnton, 2008). While direct observation methodology could have been adopted, it would have undermined the exploratory character of this research and the attempt to allow for a large variety of narratives. 9.4 Suggested future research A number of future research directions could be identified through this work as follows. Despite the body of existing research and evidence presented through this work, there appears to be still no clearly agreed best practice, within the literature, on how to ultimately support the adoption of more energy efficient behaviour at home. Practitioners are equipped with a range of intervention strategies, but the difficulty faced is to understand which one should be used in relation to the vast range of underlying and impacting determinants, in order to encourage the adoption of more energy efficient behaviour. While
  • 225. 9. Conclusion 205 some previous research has demonstrated that certain intervention strategies did, or did not, produce changes in behaviour, they mostly could not sufficiently explain how change came about and led to the desired adoption, whether short or long-term, of more energy efficient behaviour. The findings of this research have challenged the potential impact of strategies, such as information provision, but also shown the potential that community-based initiatives appear to have, as they tend to focus on the importance of social networks for circulating information and expectations, regarding appropriate behaviour. These are fields that, therefore, might be further explored, for example through the use of smart technologies. This research has also shown that if the rate of adoption of more energy efficient behaviour is to increase, that interventions, focusing on providing information or financial incentives, are unlikely to work for a large proportion of energy users. Consideration might thus be given to exploring how self-efficacy could be increased and, most importantly, how strategies of reduced energy use developed. This study acknowledged the number of programmes and interventions that have been implemented in Portugal (1.7.). Nevertheless little evidence could be found in terms of the impact of such interventions within the scope of this research, and thus future studies might want to advance on this.
  • 226. References 206 References Abrahamse, W. (2003). The effect of tailored information goal setting and feedback on household energy use. In L. Hendrickx, W. Jager & L. Steg (Eds.), Human decision making and environmental perception. Understanding and assisting human decision making in real-life settings (pp. 183-201). Groningen: Department of Psychology, University of Groningen. Abrahamse, W. (2007). Energy conservation through behavioral change: Examining the effectiveness of a tailor-made approach. University Library of Groningen. Retrieved from http://dissertations.ub.rug.nl/faculties/gmw/2007/w.abrahamse/. Abrahamse, W., & Steg, L. (2009). How do socio-demographic and psychological factors relate to households’ direct and indirect energy use and savings? Journal of Economic Psychology, 30(5), 711-720. Abrahamse, W., Steg, L., Vlek, C., & Rothengatter, T. (2005). A review of intervention studies aimed at household energy conservation. Journal of Environmental Psychology, 25(3), 273-291. Abrahamse, W., Steg, L., Vlek, Ch., & Rotehengatter, T. (2007). The effect of tailored information, goal setting, and tailored feedback on household energy use, energy-related behaviours, and behavioural antecedents. Journal of Environmental Psychology, 27(4), 265-276. ACEEE. (n.d.). Glossary. Retrieved 18 of February, 2013, from http://aceee.org/glossary. ADENE. (2013). Guia da eficiência energética. Lisbon: Agência para a Energia. ADENE. (n.d.). Planos e programas. Retrieved 22 of June, 2015, from http://www.adene.pt/planos-e- programas. Ajzen, I. (1991). The theory of planned behavior. Organizational Behavior and Human Decision Processes, 50, 179-211. Ajzen, I., & Fishbein, M. (1980). Understanding attitudes and predicting social behavior. Englewood Cliffs, NJ: Prentice-Halls. Ajzen, I., & Madden, T. J. (1986). Prediction of goal-directed behavior: Attitudes, intentions, and perceived behavioral control. Journal of Experimental Social Psychology, 22, 453-474. Ackermann, M. E. Ackermann (2002). Cool Comfort: America's Romance With Air-Conditioning. Washington, D.C. and London: Smithsonian Institution Press. Allen, J. B., & Ferrand, J. L. (1999). Environmental locus of control, sympathy, and proenvironmental behavior. Environment and Behavior, 31, 338–353. Anderson, C.A. (2007). Belief perseverance Encyclopedia of Social Psychology (pp. 109-110). Thousand Oaks, CA: Sage. Andreasen, A. R. (1995). Marketing social change: Changing behavior to promote health, social development, and the environment. San Francisco: Jossey-Bass. APA [American Psychological Association Task Force on the Interface Between Psychology and Global Climate Change]. (2009). Psychology and global climate change: Addressing a multi-faceted phenomenon and set of challenges. Retrieved from http://www.apa.org/science/about/publications/climate-change.aspx.
  • 227. References 207 Backhaus, J., Breukers, S., Mont, O., Paukovic, M., & Mourik, R. (2012). Sustainable Lifestyles: today's facts and tomorrow's trends. SPREAD Sustainable Lifestyles 2050 consortium (pp. 160). The Netherlands: Energy research Centre of the Netherlands. Baird, J. C., & Brier, J. M. . (1981). Perceptual awareness of energy requirements of familiar object. Journal of Applied Psychology, 66, 90-96. Baker, S. L., & Kirsch, I. (1991). Cognitive mediators of pain perception and tolerance. Journal of Personality and Social Psychology, 61(3), 504. Bamberg, M. (2003). Positioning with Davie Hogan – Stories, Tellings, and Identities. In C. Daiute & C. Lightfoot (Eds.), Narrative analysis: Studying the development of individuals in society (pp. 135- 157). London, UK: Sage Publications. Bamberg, S., Ajzen, I., & Schmidt, P. (2003). Choice of travel mode in the theory of planned behavior: The roles of past behavior, habit, and reasoned action. Basic and applied social psychology, 25(3), 175- 187. Bandura, A. (1977a). Self-efficacy: Toward a unifying theory of behavioural change. Psychological Review, 94(2), 191-215. Bandura, A. (1977b). Social Learning Theory. Englewood Cliffs, NJ: Prentice Hall. Bandura, A. (1982). Self-efficacy mechanism in human agency. American psychologist, 37(2), 122. Bandura, A. (1986). Social Foundations of Thought and Action: A Social Cognitive Theory. Englewood Cliffs, NJ: Prentice-Hall. Bandura, A. (1990). Selective activation and disengagement of moral control. Journal of Social Issues, 46, 27-46. Bandura, A. (1992). Observational learning. In L. R. Squire (Ed.), Encyclopedia of learning and memory. New York: Macmillan. Barenergy (2011). Barriers to changes in energy behaviour among end consumers and households. Final Report. Barr, S., & Gilg, A.W. (2006). Sustainable Lifestyles: framing environmental action in and around the home. Geoforum, 37(6), 906-920. BBC News. (2010). Climate scepticism 'on the rise'. BBC poll shows. Retrieved 08 of July, 2012, from http://news.bbc.co.uk/2/hi/8500443.stm. BBC World Service Poll. (2007). All Countries Need to Take Major Steps on Climate Change: Global Poll PIPA, Global Scan. Becker, L. J. (1978). Joint effect of feedback and goal setting on performance: A field study of residential energy conservation. Journal of Applied Psychology, 63(4), 428-433. Becker, L. J., Seligman, C., Fazio, R. H., & Darley, J. M. (1981). Relating attitudes to residential energy use. Environment and Behavior, 13, 590-609. Bergman, M. M. (2010). On Concepts and Paradigms in Mixed Methods Research. Journal of Mixed Methods Research, 4(3), 171-175. Bergman, M. M. (2011). The Good, the Bad, and the Ugly in Mixed Methods Research and Design. Journal of Mixed Methods Research, 5(4), 271-275. Berkhout, P.H.G., Muskens, J.C., & Velthuijsen, J. W. (2000). Defining the rebound effect. Energy Policy, 28(6-7), 425-432.
  • 228. References 208 Binswanger, M. (2001). Technological progress and sustainable development: what about the rebound effect? Ecological economics, 36(1), 119-132. Bittle, R. G., Valesano, R., & Thaler, G. (1979). The effects of daily cost feedback on residential electricity consumption. Behavior Modification, 3(2), 187-202. Black, J. S., Stern, P. C., & Elworth, J. T. (1985). Personal and contextual influences on household energy adaptations. Journal of Applied Psychology, 70(1), 3-21. Boardman, Brenda. (1991). Fuel poverty: from cold homes to affordable warmth. London, UK: Belhaven Press. Boardman, Brenda. (2010). Fixing Fuel Poverty: Challenges and Solutions. London, UK: Earthscan. BPIE. (2011). Europe's buildings under the microscope: Buildings Performance Institute Europe (BPIE). Brandon, G., & Lewis, A. (1999). Reducing household energy consumption: a qualitative and quantitative field study. Journal of Environmental Psychology, 19(1), 75-85. Brehm, J. W. (1972). Responses to loss of freedom: A theory of psychological reactance. New York: General Learning. Brehm, S., & Kassin, S. (1996). Social Psychology (3rd ed.). Boston: Houghton Mifflin Company. Brook Lyndhurst. (2007). Defra Waste & Resources R&D Programme - Lifestyle Scenarios: the Futures for Waste Composition. Summary Report. A project for Defra’s WREP: Brook Lyndhurst Ltd. Brookes, L. (2000). Energy efficiency fallacies revisited. Energy Policy, 28(6), 355-366. Brouwer, R., Brander, L. M., & van Beukering, P. (2008). “A convenient truth”: Air travel passengers willingness to pay to offset their CO2 emissions. Climatic Change, 90(3), 299-313. Burgess, J., & Nye, M. (2008). Rematerialising energy use through transparent monitoring systems. Energy Policy, 36(12), 4454-4459. Burns, D., (2006) ‘Evaluation in complex governance arenas: the potential of large system action research’, in B. Williams and I. Imam, Using systems concepts in evaluation, Fairhaven, MA: American Evaluation Association. BusinessDictionary. (n.d.). Energy Conservation. Business Dictionary. Retrieved 12 of February, 2013, from http://www.businessdictionary.com/definition/energy-conservation.html. Buzar, S. (2007a). Energy Poverty in Eastern Europe: Hidden Geographies of Deprivation. Aldershot: Ashgate. Buzar, S. (2007b). The ‘hidden’geographies of energy poverty in post-socialism: between institutions and households. Geoforum, 38(2), 224-240. Buzar, S. (2007c). When homes become prisons: the relational spaces of postsocialist energy poverty. Environment and Planning A, 39(8), 1908-1925. Campbell, C. (1995). The Sociology of Consumption Acknowledging Consumption (pp. 96-126). London and New York: Routledge. Carey, S. (1986). Cognitive science and science education. American Psychologist, 41(10), 1123-1130. Carpenter, S. R., Folke, C., Scheffer, M., & Westley, F. (2009). Resilience: accounting for the noncomputable. Ecology & society, 14(1), 13. Cassiani, S., Zanetti, M., & Pelá, N. (1992). The telephone survey: a methodological strategy for obtaining information. Journal of Advanced Nursing, 17, 576-581.
  • 229. References 209 Chaiken, S., & Trope, Y. (1999). Dual Process Theories in Social Psychology. New York: Guilford Publications. Chappells, H. & Shove, E. (2005). Building Research & Information, 33(1), p. 32-40 p. Chatterton, T. (2011). An Introduction to Thinking About ‘Energy Behaviour’: a multi-model approach (pp. 39). London, UK: Department of Energy and Climate Change. Cialdini, R. B. (1993). Influence (rev): The Psychology of Persuasion: HarperCollins. Cialdini, R. B. (2001). Influence: Science and Practice (4th ed.). Boston, MA: Allyn & Bacon. Cialdini, R. B., Kallgren, C. A., & Reno, R. R. (1991). A focus theory of normative conduct: A theoretical refinement and reevaluation of the role of norms in human behavior. Advances in experimental social psychology, 24(20), 1-243. Cialdini, R. B., Reno, R. R., & Kallgren, C. A. (1990). A focus theory of normative conduct: Recycling the concept of norms to reduce littering in public places. Journal of personality and social psychology, 58(6), 1015-1026. Cialdini, R. B., & Trost, M. R. . (1998). Social influence: Social norms, conformity and compliance. In D. T. Gilbert & S. T. Fiske (Eds.), The handbook of social psychology (4th ed., Vol. 2, pp. 151-192). New York: McGraw-Hill. Clough, P., and Nutbrown, C. (2007) A student’s guide to methodology. London: Sage Publications. ISBN 0 978-1-4129-2912-7. Cohen, L., Manion, L., & Morrison, K. (2000). Research methods in education (pp. 245). London: Routledge Falmer. Cole, S. A. (2006). Witnessing Creation. Social Studies of Science, 36(6), 855-860. Cole. R. J. (2011). Motivating stakeholders to deliver environmental change. Building Research & Information, 39(5), 431-435 CCC. (2012). How local authorities can reduce emissions and manage climate risk (pp. 96). London, UK: Committee on Climate Change. Cooper, H. (1998). Synthetizing research: a guide for literature reviews (3rd ed.). Beverly Hills, CA: Sage. Corti, L. (1993). Using diaries in social research. Social research update, 3(2). Creswell, J. W. (2009). Research Design: Qualitative, Quantitative and Mixed Methods Approaches. London: Sage Publications. Creswell, J. W., & Clark, V. L. P. (2007). Designing and conducting mixed methods research. Thousand Oaks, CA: Sage publications. Creswell, J. W., & Miller, D. L. (2000). Determining validity in qualitative inquiry. Theory into practice, 39(3), 124-131. Crosbie, T., & Baker, K. (2010). Energy-efficiency interventions in housing: learning from the inhabitants. Building Research & Information, 38(1), 70-79. Dainton, M., & Zelley, E. (2005). Applying communications theory for professional life. Thousand Oaks: Sage. Darby, S. (2005). Social learning and public policy: Lessons from an energy-conscious village. Energy Policy, (34), 2929-2940. Darby, S. (2006). The Effectiveness of feedback on Energy Consumption: A review for DEFRA of the literature on metering, billing and direct displays (pp. 24): Environmental Change Institute, University of Oxford (available at: http://www.defra.gov.uk/environment/energy/research/).
  • 230. References 210 Darby, S. (2010). Smart metering: what potential for householder engagement?, Building Research & Information, 38:5, 442-457. Darley, J. M., & Latane, B. (1968). Bystander intervention in emergencies: diffusion of responsibility. Journal of personality and social psychology, 8(4p1), 377. Darnton, A. (2008). Reference Report: An overview of behaviour change models and their uses In S. S. i. G. Government Social Research (Ed.), GSR Behaviour Change Knowledge Review: Centre for Sustainable Development, University of Westminster. Darnton, A., Verplanken, B., White, P., & Whitmarsh, L. E. (2011). Habits, Routines and Sustainable Lifestyles: A summary report to the Department for Environment, Food and Rural Affairs. London, UK: A. D. Research and Analysis for Defra. Dawson, C. (2002). Practical research methods: A user-friendly guide to mastering research. Oxford: How To Books Ltd. ISBN 1-85703-829-0. Dawson, T. L. (2002). New tools, new insights: Kohlberg's moral reasoning stages revisited. International Journal of Behavior Development, 26(2), 154-166. de Dear, R. J., & Brager, G. (2001). The adaptive model of thermal comfort and energy conservation in the built environment. International Journal of Biometeorology, 45(2), 100-108. de Groot, J. I., Steg, L., & Dicke, M. (2007). Morality and Reducing Car Use: Testing the Norm Activation Model of Prosocial Behavior. In F. Columbus (Ed.), Transportation Research Trends: NOVA Publishers. DECC. (2011). Great Britain’s housing energy fact file In J. Palmer & I. Cooper (Eds.), (pp. 118): Department of Energy & Climate Change (DECC). DECC. (2012). Public attitudes tracking survey: wave 2 Public attitudes tracking survey: Department of Energy & Climate Change (DECC). DEFRA. (2007). Survey of Public Attitudes and Behaviours toward the Environment: 2007. London: Department for Environment, Food and Rural Affairs (DEFRA). DEFRA. (2008). A Framework for Pro-Environmental Behaviours Report. London: Department for Environment, Food and Rural Affairs (DEFRA). Denzin, N., & Lincoln, Y. S. (2002). Handbook of Qualitative Research. London: Sage Publications. DCLG. (2012). Definitions of general housing terms. Definitions for local authorities compiling data. Retrieved 12 of January, 2013, from https://www.gov.uk/definitions-of-general-housing-terms. Deutsch, M. (2010). Life Cycle Cost Disclosure, Consumer Behavior, and Business Implications. Journal of Industrial Ecology, 14(1), 103-120. DGEG. (2010). National Energy Characterization. Retrieved 11 of February, 2012, from http://www.dgge.pt/. DGGE/IP-3E. (2004). Eficiência energética em equipamentos e sistemas eléctricos no sector residencial. Lisbon: Direcção Geral de Geologia e Energia (DGGE). Dholakia, R. R., & Dholakia, N. (1983). From social psychology to political economy: A model of energy use behavior. Journal of Economic Psychology, 3, 231-247. Diekmann, A., & Meyer, R. (2008). Schweizer Umweltsurvey 2007. Dokumentation und Codebuch (Swiss Environmental Survey 2007. Documentation and code book). Zurich: Professorship for Sociology, ETH. Dobson, A. (2011). Sustainability Citizenship (G. House Ed.). United Kingdom: Green House.
  • 231. References 211 Dolan, P.; Hallsworth, M.; Halpern, D.; King, D.; Vlaev, I. (2010). Mindspace - Influencing behaviour through public policy. Donn, J. (1999). Frustration sapping environmental concern, researcher says: Associated Press state and local wire. Dwyer, W. O., Leeming, F. C., Cobern, M. K., Porter, B. E., & Jackson, J. M. (1993). Critical review of behavioral interventions to preserve the environment. Research since 1980. Environment and Behavior, 25(5), 275-321. Easterby-Smith, M., Thorpe, R., & Lowe, A. (2002). Management Research: An Introduction. London, UK: Sage Publications. EEA. (2004). EEA Signals 2004 - A European Environment Agency update on selected issues. Copenhagen: European Environment Agency (EEA), Office for Official Publications of the European Communities (OPOCE). EEA. (2008). Energy and environment report 2008. Copenhagen: European Environment Agency (EEA). EEA. (2011). Final energy consumption by sector in the EU-27, 1990-2008. Retrieved 12 of February, 2012, from http://www.eea.europa.eu/data-and-maps/figures/final-energy-consumption-by-sector-4. EEA. (2013). Achieving Energy Efficiency through behaviour change: what does it take? Copenhagen: European Environment Agency (EEA). EIA. (2013). Glossary. U.S. Energy Information Administration. Retrieved 12 of February, 2013, from http://www.eia.gov/tools/glossary/index.cfm. ECI. (2005). 40% house. Oxford, UK. Elkington, J. (1997). Cannibals with Forks: the Triple Bottom Line of 21st Century Business. New York: Capstone Publishing Ltd. Energaia (2008). Energyprofiler: Perfil energético do sector residencial. ENERGAIA, Agência de Energia do Sul da Área Metropolitana do Porto. Energy Saving Trust. (2011). The rise of the machines: a review of energy using products in the home from the 1970s to today. London: Energy saving Trust. Energy Saving Trust. (2012). Powering the nation: household electricity using habits revealed. London, UK: Energy Saving Trust. Energyprofiler. (2011). Transformar atitudes em ação: Perfil Energético do Setor Residencial: ENERGAIA, Agência de Energia do Sul da Área Metropolitana do Porto. Eurobarometer. (2011a). Special Eurobarometer 365. Attitudes of European citizens towards the environment. Eurobarometer. (2011b). Special Eurobarometer 372. Climate Change. European Commission. (2010). EUR 24283 – Energy-efficient Buildings PPP Multi-annual Roadmap and longer term strategy. Luxembourg: Publications Office of the European Union. European Commission (n.d.). Energy efficiency directive. Retrieved 19 of June, 2015, from http://ec.europa.eu/energy/en/topics/energy-efficiency/energy-efficiency-directive. Eurostat. (2007). Statistics on income, social inclusion and living conditions - Ad-hoc modules (2007 module: Housing conditions). Your key to European statistics. Retrieved 10 of July, 2013, from http://epp.eurostat.ec.europa.eu/portal/page/portal/income_social_inclusion_living_conditions/d ata/ad_hoc_modules
  • 232. References 212 Eurostat. (2011). Energy Statistics Data. Retrieved 1 of October, 2011, from http://epp.eurostat.ec.europa.eu/portal/page/portal/energy/data/database Eurostat. (2013). Inability to keep home adequately warm (source: SILC). Retrieved 8 of July, 2013, from http://appsso.eurostat.ec.europa.eu/nui/show.do?dataset=ilc_mdes01&lang=en Eurostat. (2015). Consumption of energy. Retrieved 19 of June, 2015, from http://ec.europa.eu/eurostat/statistics-explained/index.php/Consumption_of_energy. Eurostat. (n.d.). Statistics explained. Energy price statistics. Retrieved 14 of July, 2013, from http://epp.eurostat.ec.europa.eu/statistics_explained/index.php/Energy_price_statistics#Natural_ gas_prices_for_industrial_consumers Eurowinter Group. (1997). Cold exposure and winter mortality from ischaemic heart disease, cerebrovascular disease, respiratory disease, and all causes in warm and cold regions of Europe. The Lancet, 349(9062), 1341-1346. ERSE. (2007). Plano de promoção da eficiência no consumo de energia elétrica para 2008. Lisbon: Entidade Reguladora dos Serviços Energético. ERSE. (2008). Medidas aprovadas PPEC 08: Plano de promoção da eficiência no consumo de energia eléctrica para 2008. Lisbon: Entidade Reguladora dos Serviços Energético. ERSE. (2009). Plano de promoção da eficiência no consumo de energia elétrica para 2009-2010. Lisbon: Entidade Reguladora dos Serviços Energético. ERSE. (2010). Plano de promoção da eficiência no consumo de energia elétrica para 2011-2012. Lisbon: Entidade Reguladora dos Serviços Energético. ERSE. (n.d.). Medidas em Implementação. Retrieved 22 of June, 2015, from http://www.erse.pt/pt/planodepromocaodaeficiencianoconsumoppec/edicoesPPEC/siteppec1112 /medidasimplementacao/Paginas/default.aspx. FAI (n.d.). Fundo de apoio à inovação. Retrieved 25 of June, 2015, from http://fai.pt/o-fai/. Feather, N. T. (1990). The psychological impact of unemployment. New York: Springer. FEE (n.d.). Fundo de eficiência energética. Retrieved 25 of June, 2015, from http://fee.adene.pt/o-que- e/Paginas/default.aspx. Feenstra, C.F.J., Backhaus, J., & Heiskanen, E. (2009). How to change consumers’ energy-related behaviour? Improving demand side management programmes via an action research approach. Paper presented at the First European Conference on Energy and Behaviour, Maastricht, The Netherlands. Feinberg, M., & Willer., R. (2010). The Good of Gossip? The Benefits of this Unlikely Prosocial Behavior. Berkeley: Department of Psychology. University of California. Festinger, L. (1957). A Theory of Cognitive Dissonance. Stanford, CA: Stanford University Press. Fischer, C. (2008). Feedback on household electricity consumption: a tool for saving energy? Energy efficiency, 1(1), 79-104. Folke, C. (2006). Resilience: The Emergence of a Perspective for Social-Ecological Systems Analyses. Global Environmental Change, 16, 253-267. Future Foundation. (2006). Energy Efficiency - Public attitude, private action: Logica. Galli, A., Kitzes, J., Wermer, P., Wackernagel, M., Niccolucci, V., & Tiezzi, E. (2007). An exploration of the mathematics behind the ecological footprint. International Journal of Ecodynamics, 2(4), 250–257.
  • 233. References 213 Gardner, G. T., & Stern, P. C. (2002). Environmental Problems and Human Behavior (2nd ed.). Boston, MA: Pearson Custom Publishing. Gardner, G. T., & Stern, P. C. (2008). The short list: The most effective actions US households can take to curb climate change. Environment: Science and Policy for Sustainable Development, 50(5), 12-25. Gärling, T., Eek, D., Loukopoulos, P., Fujii, S., Johansson-Stenman, O., Kitamura, R., Vilhelmson, B. (2002). A conceptual analysis of the impact of travel demand management on private car use. Transport Policy, 9(1), 59-70. Garvey, James. (2009). We broke it. So we own it. The Guardian. http://www.theguardian.com/commentisfree/cif-green/2009/sep/07/climate-change-10-10 Gascoigne, C., Morgan, K., Gross, H., & Goodwin, J. (2010). Reducing the health risks of severe winter weather among older people in the United Kingdom: an evidence-based intervention. Ageing & Society, 30, 275-297. Gass, R. H., & Seiter., J. S. (2003). Persuasion, Social Influence, and Compliance Gaining. Boston: Pearson Education, Inc. Gatersleben, B., Steg, L., & Vlek, C. (2002). The measurement and determinants of Environmentally significant consumer behaviour. Environment and Behaviour, 34(3), 335-362. Gatersleben, B., & Vlek, C. (1998). Household Consumption, Quality of Life and Environmental Impacts: A Psychological Perspective and Empirical Study. In T. S. Uiterkamp (Ed.), Green Households? (pp. 141-183). London: Earthscan. Gatersleben, B.C.M. (2000). Sustainable household metabolism and quality of life: Examining the perceived social sustainability of environmentally sustainable household consumption patterns. (PhD), University of Groningen, Groningen, the Netherlands. Geller, E. S. (1981). Evaluating energy conservation programs: Is verbal report enough? Journal of Consumer Research, 8, 331–335. Geller, E. S. (1992). It takes more than information to save energy. American Psychologist, 47(6), 814-815. Geller, E. S. (2002). The challenge of increasing proenvironmental behavior. In R. B. Betchel & A. Churchman (Eds.), Handbook of environmental psychology (pp. 525-540). New York: John Wiley & Sons. Geller, E. S., Berry, T. D., Ludwig, T. D., Evans, R. E., Gilmore, M. R., & Clarke, S. W. (1990). A conceptual framework for developing and evaluating behavior change interventions for injury control. Health Education Research, 5(2), 125-137. Geller, E. S., Winett, R. A., & Everett, P. B. (1982). Preserving the environment: New strategies for behavior change. Elmsford, NY: Pergamon. Geller, H., Harrington, P., Rosenfeld, A. H., Tanishima, S., & Unander, F. (2006). Polices for increasing energy efficiency: Thirty years of experience in OECD countries. Energy Policy, 34(5), 556-573. Gerdes, J. (2009). Energy Efficiency Policies and Measures in The Netherlands. Petten: ECN, ODYSSEE- MURE, Intelligent Energy Europe. Gibbs, Anita. (1997). Focus groups. Social research update, 19(8). Giddens, A. (1984). The Constitution of Society – outline of the theory of structuration. Berkeley and Los Angeles: University of California Press. Gifford, R., Iglesias, F., & Casler, J. (2008). Psychological barriers to pro-environmental behavior: The development of a scale. Paper presented at the Annual meeting of the Canadian Psychological Association, Montreal, QC.
  • 234. References 214 Giorgi, S., Fell, D., Austin, A., & Wilkins, C. (2009). EV0402: public understanding of links between climate change and (i) food and (ii) energy use: final report. A report to the Department for Environment, Food and Rural Affairs. London: Brook Lyndhurst & Defra. Glasersfeld, E. von (1989). “Cognition, Construction of Knowledge and Teaching.” Synthese, 80(1), 121-140. Glasersfeld, E. von (1990). “Environment and Education.” In L.P. Steffe & T. Wood (eds.), Transforming Children’s Mathematics Education: International Perspectives, (pp. 200-215). Hillsdale, NJ: Lawrence Erlbaum. Golafshani, N. (2003). Understanding Reliability and Validity in Qualitative Research. The Qualitative Report, 8(4), 597-607. Goldblatt, David L. (2005). Sustainable Energy Consumption and Society - Personal, Technological, or Social Change? Washington DC, USA: Springer. Gottron, F. (2001). Energy Efficiency and the Rebound Effect: Does Increasing Efficiency Decrease Demand CRS Report for Congress (pp. 1-4). Green Alliance. (2011). Green Alliance policy insight. Grier, S., & Bryant, C. (2005). Social marketing in public health. Public Health, 26, 319-339. Grist, M. (2010). Changing the Subject, How new ways of thinking about human behaviour might change politics, policy and practice. London: RSA. Grubb, M. J. (1990). Communication energy efficiency and economic fallacies. Energy Policy, 18(8), 783-785. Guagnano, G. A. (2001). Altruism and market-like behavior: An analysis of willingness to pay for recycled paper products. Population and Environment, 22, 425-438. Guertin, C., Kumbhakar, S., & Duraiappah, A. (2003). Determining Demand for Energy Services: Investigating income - driven behaviours: International Institute for Sustainable Development. Hardin, G. (1968). The Tragedy of the Commons. Science, New Series, 162(3859), 1243-1249. Hargreaves, T. (2012). Opening the black box of the household: Understanding how householders interact with feedback from smart energy monitors 3S Working Paper. Norwich. Hargreaves, T., Nye, M., & Burgess, J. (2010). Making energy visible: A qualitative field study of how householders interact with feedback from smart energy monitors. Energy Policy, 38(10), 6111- 6119. Harrington, B. E., Heyman, B., Merleu-Ponty, N., Stockton, H., Ritchie, N., & Heyman, A. (2005). Keeping warm and staying well: findings from the qualitative arm of the Warm Homes Project. Health & social care in the community, 13(3), 256-267. Hastings, G., & Saren, M. (2003). The Critical Contribution of Social Marketing: Theory and Application. Marketing Theory, 3(3), 305-322. Hastings, G.B., & Haywood, A.J. (1991). Social marketing and communication in health promotion. Health Promotion International, 6, 135-145. Healy, J. D. (2003). Excess winter mortality in Europe: a cross country analysis identifying key risk factors. Journal of Epidemiology and Community Health, 57(10), 784-789. Healy, J. D. (2004). Housing, Fuel Poverty And Health: A Pan-European Analysis. London: Ashgate. Heberlein, T. A., & Warriner, G. K. . (1983). The influence of price and attitude on shifting residential electricity consumption from on-to off-peak periods. Journal of Economic Psychology, 4(1), 107- 130.
  • 235. References 215 Heiskanen, E., Johnson, M., & Vadovics, E. (2009). Creating Lasting Change in Energy Use Patterns through Improved User Involvement. Paper presented at the Joint Actions on Climate Change Conference, Aalborg, Denmark. Heiskanen, E., Mourik, R., Feenstra, Y., & Pariag, J. (2009). BEYOND INDIVIDUAL BEHAVIOURAL CHANGE – WHY AND HOW? European council for an energy efficient economy (ECEEEE), Energy Efficiency and Behaviour. http://www.eceee.org/library/conference_proceedings/EE_and_Behaviour/2009/Panel_7/7.702 Helmig, B., & Thaler, J. (2010). On the effectiveness of social marketing – what do we really know? Journal of Nonprofit & Public Sector Marketing, 22(4), 264-287. Herring, H. (2006). Energy efficiency - a critical view. Energy, 31(1), 10-20. Higgins, E. T. (1987). Self-discrepancy: a theory relating self and affect. Psychological review, 94(3), 319-340. Hitchings, R. (2009). Studying thermal comfort in context. Building Research and Information, 37(1), 89-94. Homans, J. (1958). Social Behavior as Exchange. American Journal of Sociology, 63, 597-606. Huebner, Gesche M., Cooper, Justine, & Jones, K. (2011). Energy saving practices, barriers against and reasons for change among social housing tenants. Paper presented at the Research student's conference on "Buildings don't use energy, people do?" - domestic energy use and CO2 emissions in existing dwellings, Bath, UK. Hussey, J., & Hussey, R. (1997). Business Research: A Practical Guide for Undergraduate and Postgraduate Students. London: Macmillan. INE. (2011). Anuário Estatístico de Portugal 2010. Lisbon: Instituto Nacional de Estatística, I.P. (INE). INE (2012). Orçamentos Familiares - Inquérito às despesas das famílias - 2010 / 2011. Retrieved 28/10/2013, from Instituto Nacional de Estatística http://www.ine.pt/xportal/xmain?xpid=INE&xpgid=ine_publicacoes&PUBLICACOESpub_boui=1415 77698&PUBLICACOESmodo=2&xlang=pt. INE I.P./DGEG. (2011). Inquérito ao Consumo de Energia no Sector Doméstico 2010 Estatísticas Oficiais. Lisbon, Portugal. IPCC. (2007). Climate Change 2007 - Impacts, Adaptation and Vulnerability: Working Group II contribution to the Fourth Assessment Report of the IPCC (M. L. Parry, O. F. Canziani, J. P. Palutikof, P. J. van der Linden & C. E. Hanson Eds. 1st ed.). Cambridge, UK: Cambridge University Press. IPPR. (2009). Addressing Climate Change through Sustainable Development. U.S. Department of State e- journal USA - Climate Change Perspectives. www.ippr.org IUCN, UNEP, & WWF. (1991). Caring for the Earth: A Strategy for Sustainable Living. London: World Conservation Union (IUCN), United Nations Environment Programme (UNEP), World Wide Fund for Nature (WWF). Jackson, T. (2005). Motivating Sustainable Consumption: a review of evidence on consumer behaviour and behavioural change: University of Surrey. Jager, W., Janssen, M., Vries, H. D., Greef, J. D., & Vlek, C. (2000). Behaviour in commons dilemmas: Homo economicus and Homo psychologicus in an ecological-economic model. Ecological Economics, 35(3), 357-379. Janda, K. B. (2011). Buildings don't use energy: people do, Architectural Science Review, 54(1), 15-22 Jeannerod, M. (2003). The mechanism of self-recognition in humans. Behavioural brain research, 142(1), 1- 15.
  • 236. References 216 Kahneman, D., & Tversky, A. (1979). Prospect theory: An analysis of decision under risk. Econometrica: Journal of the Econometric Society, 47(2), 263-291. Kaplan, S. (2000). New ways to promote proenvironmental behavior: Human nature and environmentally responsible behavior. Journal of social issues, 56(3), 491-508. Kates, R. W., Clark, W. C., Corell, R., Hall, J. M., Jaeger, C. C., Lowe, I., Svedin, U. (2001). Sustainability science. Science, New Series, 292(5517), 641-642. Kempton, W., Boster, J. S., & Hartley, J. A. (1995). Environmental Values in American Culture. Cambridge, MA: The MIT Press. Kempton. W., & Montgomery, L. (1982). Folk quantification of energy. Energy 7(10), 917-927. Kempton, W., Reynolds, C., Fels, M., & Hull, D. (1992). Utility control of residential cooling: resident- perceived effects and potential program improvements. Energy and buildings, 18(3), 201-219. Kennedy, L. (2011). Sustainable Development. louiskennedy - Just another WordPress.com site. Retrieved 5 of February, 2012, from http://louiskennedy.wordpress.com/2011/01/26/back-again/ Khazzoom, J. Daniel. (1980). Economic Implications of Mandated Efficiency Standards for Household Appliances. The Energy Journal, 1(4), 21-40. Kitzes, J., Galli, A., Bagliani, M., Barrett, J., Dige, G., Ede, S., Wiedmann, T. (2009). A research agenda for improving national Ecological Footprint accounts. Ecological Economics, 68(7), 1991-2007. Knott, David, Muers, Stephen, & Aldridge, Stephen. (2008). Achieving Culture Change: A Policy Framework, A discussion paper by the Strategy Unit (pp. 138). London: Strategy Unit, Cabinet Office. Kollmuss, A., & Agyeman, J. (2002). Mind the gap: why do people act environmentally and what are the barriers to pro-environmental behavior? Environmental Education Research, 8(3), 239-260. Kollock, P. (1998). Social Dilemmas: The Anatomy of Cooperation. American Review of Sociology, 24, 183- 214. Kotler, P., Roberto, E. L. , & Roberto, N. . (1989). Social marketing: strategies for changing public behavior: Free Press. Kotler, P., & Zaltman, G. (1971). Social marketing: an approach to planned social change. The Journal of Marketing, 35(3), 3-12. KPMG. (2012). Expect the unexpected: Building business value in a changing world. http://www.kpmg.com/global/en/issuesandinsights/articlespublications/pages/building-business- value.aspx Kurz, T. (2002). The psychology of environmentally sustainable behavior: Fitting together pieces of the puzzle. Analyses of Social Issues and Public Policy, 2(1), 257-278. Leal Filho, W. (2011). About the Role of Universities and Their Contribution to Sustainable Development. Higher Education Policy, 24(4), 427-438. Leedy, P., & Ormrod, J. E. (2001). Practical research: Planning and design (7th ed.). Upper Saddle River, New Jersey: Prentice-Hall. Lehman, P. K., & Geller, E. S. (2004). Behavior analysis and environmental protection: accomplishments and potential for more. Behavior and Social Issues, 13(1), 13-32. Leiserowitz, A. (2007). Public Perception, Opinion and Understanding of Climate Change – Current Patterns, Trends and Limitations Human Development Report 2007/2008 - Fighting climate change: Human solidarity in a divided world.
  • 237. References 217 Leiserowitz, A., Maibach, E., & Roser-Renouf, C. (2009). Saving Energy at Home and on the Road: A Survey of Americans’ Energy Saving Behaviors, Intentions, Motivations, and Behaviors. Yale Project on Climate Change. Leiserowitz, A., Maibach, E., Roser-Renouf, C., & Smith, N. (2011a). Climate change in the American Mind: Americans’ global warming beliefs and attitudes in May 2011. In Y. P. o. C. C. Yale Project on Climate Change Communication (Ed.). New Haven, CT: University and George Mason University. Leiserowitz, A., Maibach, E., Roser-Renouf, C., Smith, N., & Hmielowski, J. D. (2011b). Climate change in the American Mind: Public support for climate & energy policies in November 2011. New Haven, CT: Yale University and George Mason University. Lewis, D. (1969). Convention: A Philosophical Study. Cambridge: Harvard University Press. Lindenberg, S., & Steg, L. (2007). Normative, gain and hedonic goal frames guiding environmental behavior. Journal of Social issues, 63(1), 117-137. Linville, P.W., & Fischer, G.W. (1991). Preferences for separating and combining events: a social application of prospect theory and the mental accounting model. Journal of Personality and Social Psychology, 60, 5-23. Litoselliti, L. (2003). Using Focus Group in Research: Continuum. Lomas, K. J. (2010). Editorial: Carbon reduction in existing buildings: A transdisciplinary approach. Building Research and Information, 38(1), 1-11. Lorenzoni, I., & Pidgeon, N. F. (2006). Public views on climate change: European and USA perspectives. Climatic Change, 77(1-2), 73-95. Lovins, A. B. (1998). Further comments on red herrings. Letter to the New Scientist(2152), 18. Lovins, A. B., Henly, J., Ruderman, H., & Levine, M. D. (1988). Energy saving resulting from the adoption of more efficient appliances: another view; a follow-up. Energy Journal, 9(2), 155. Lutzenhiser, L. (1993). Social and behavioral aspects of energy use. Annual Review of Energy and the Environment, 18(1), 247-289. Lutzenhiser, L. (2002). Marketing Household Energy Conservation: The Message and the Reality. In T. Dietz & P. C. Stern (Eds.), New Tools for Environmental Protection: Education, Information, and Voluntary Measures. Washington, D.C.: National Academy of Sciences. Maddux, J. E. (1995). Self-Efficacy theory: An introduction. In J. E. Maddux (Ed.), Self-Efficacy, Adaptation, and Adjustment: Theory, Research, and Application (pp. 3-33). New York: Plenum Press. Magalhães, S., & Leal, V. (2012). EPBD assessment as a tool for fuel poverty estimation. Paper presented at the IAIA12, Porto, Portugal. Maibach, E., Roser-Renouf, C., & Leiserowitz, A. (2009). Global Warming’s Six Americas 2009: An audience segmentation. New Haven, CT: Yale Project on Climate Change, George Mason University Center for Climate Change Communication. Maréchal, K. (2010). Not irrational but habitual: The importance of "behavioural lock-in" in energy consumption. Ecological Economics, 69(5), 1104-1114. Marshall, G., & Lynas, M. (2003). Why we don't give a damn from http://www.newstatesman.com/node/146820 Martiskainen, M. (2007). Affecting consumer behaviour on energy demand. Brighton, East Sussex: University of Sussex.
  • 238. References 218 Marx, S. M., Weber, E. U., Orlove, B. S., Leiserowitz, A., Krantz, D. H., Roncoli, C., & Phillips, J. (2007). Communication and mental processes: Experiential and analytic processing of uncertain climate information. Global Environmental Change, 17(1), 47-58. Matthies, E., Klöckner, C. A., & Preißner, C. L. (2006). Applying a modified moral decision making model to change habitual car use: how can commitment be effective? Applied Psychology, 55(1), 91-106. McCalley, L. T., & Midden, C. J. H. (2002). Energy conservation through product-integrated feedback: The roles of goal-setting and social orientation. Journal of Economic Psychology, 23(5), 589–603. McCarty, John A., & Shrum, L. J. (1993). A Structural Equation Analysis of the Relationships of Personal Values, Attitudes and Beliefs about Recycling, and the Recycling of Solid Waste Products. In L. McAlister & M. Rothschild (Eds.), Advances in Consumer Research (Vol. 20, pp. 641-646). Provo, UT: Association for Consumer Research. McKenzie-Mohr, D. (2000). New ways to promote proenvironmental behavior: Promoting sustainable behavior: An introduction to community-based social marketing. Journal of Social Issues, 56(3), 543-554. McKenzie-Mohr, D., & Smith, W. (1999). Fostering sustainable behavior: An introduction to community- based social marketing (2nd ed.). Gabriola Island, British Columbia, Canada: New Society. McMahon, T. (2007) ‘Is reflective practice synonymous with action research?’, Educational Action Research, Vol.7(1), pp.163 - 169. McMakin, A. H., Malone, E. L., & Lundgren, R. E. (2002). Motivating residents to conserve energy without financial incentives. Environment and Behavior, 34(6), 848-863. McMichael, A., Woodruff, R., & Hales, S. (2006). Climate change and human health: present and future risks. The Lancet, 367(9513), 859-869. Merton, R., & Kendall, P. (1987). The Focused Interview. American Journal of Sociology, 51, 541-557. Middlemiss, L. (2008). Influencing individual sustainability: a review of the evidence on the role of community-based organisations. International Journal of Environment and Sustainable Development, 7(1), 78-93. Mill, J. S. (1836). On the Definition of Political Economy, and on the Method of Investigation Proper to It. London and Westminster Review. Miller, G. R. (2002). On Being Persuaded: Some Basic Distinctions. In J. P. Dillard & M. Pfau (Eds.), The Persuasion Handbook: Developments in Theory and Practice (pp. 3-16). Thousand Oaks, CA: Sage. Mischler, E. G. (1986). Research Interviewing: Context and Narrative: Harvard University Press. Morgan, D. (1998). The Focus Group Guidebook. London: Sage Publications. Morgan, D. (2007). Paradigms Lost and Pragmatism Regained : Methodological Implications of Combining Qualitative and Quantitative Methods. Journal of Mixed Methods Research, 1, 48-76. Morgan, D. L., Krueger, R. A., & King, J. A. (1998). Analyzing and Reporting Focus Group Results. London, UK: Sage Publications. Morgan, M. G., Fischhoff, B., Bostrom, A., & Atman, C. J. (2002). Risk Communication: A Mental Models Approach. Cambridge: Cambridge University Press. Morse, J. M. (2003). Principles of mixed methods and multimethod reseacrh method. In A. Tashakkori & C. Teddlie (Eds.), Handbook of mixed methods in social & behavioral research (pp. 189-208). London: Sage Publications.
  • 239. References 219 Moser, S. C. (2007). More bad news: The risk of neglecting emotional responses to climate change information. In S. C. Moser & L. Dilling (Eds.), Creating a climate for change: Communicating climate change and facilitating social change (pp. 64-80). New York: Cambridge University Press. Moser, S.C., & Dilling, L. (2004). Making Climate Hot: Communicating the Urgency and Challenge of Global Climate Change. Environment, 46(10), 32-46. Nakajima, T., & Hamori, S. (2010). Change in consumer sensitivity to electricity prices in response to retail deregulation: a panel empirical analysis of the residential demand for electricity in the United States. Energy policy, 38(5), 2470-2476. Nolan, J. M. (2010). “An Inconvenient Truth” increases knowledge, concern, and willingness to reduce greenhouse gases. Environment and Behavior, 42(5), 643-658. Nordlund, A. M., & Garvill, J. (2002). Value structures behind proenvironmental behavior. Environment and Behavior, 34(6), 740-756. Nordlund, A. M., & Garvill, J. (2003). Effects of values, problem awareness, and personal norm on willingness to reduce personal car use. Journal of environmental psychology, 23(4), 339-347. Norwegian Ministry of the Environment. (1994). Symposium on Sustainable Consumption. Oslo Roundtable on Sustainable Production and Consumption. http://www.iisd.ca/consume/oslo004.html Nye, M. , Whitmarsh, L. , & Foxon, T. (2010). Sociopsychological perspectives on the active roles of domestic actors in transition to a lower carbon electricity economy. Environment and Planning, 42(3), 697 – 714. O’Keefe, D. J. (1990). Persuasion: theory and research. Michigan: Sage Publications. O’Keefe, D. J. (2002). Guilt as a mechanism of persuasion. In J. P. Dillard & M. Pfau (Eds.), The persuasion handbook: Developments in theory and practice (pp. 329-344). Thousand Oaks, CA: Sage. Odyssee, & MURE. (2011). Energy Efficiency Policies in the European Union - Lessons from the Odyssee- Mure Project: Intelligent Energy Europe, APEMS. OECD. (2012). Taxing Energy Use: A graphical analysis. http://www.oecd.org/tax/tax- policy/taxingenergyuse.htm Ølander, C. F., & Thøgersen, J. (1995). Understanding of consumer behaviour as a prerequisite for environmental protection. Journal of Consumer Policy, 18(4), 345-385. OnePlanetLiving. (n.d.). Retrieved 08 of July, 2013, from http://www.oneplanetliving.org/index.html. OSF. (2013). Energy consumption [e-publication]. ISSN=1798-6869. Helsinki: Statistics Finland [referred: 29.10.2013]. Access method: http://www.stat.fi/til/ekul/kas_en.html Osterhus, T. L. (1997). Pro-Social Consumer Influence Strategies: When and How Do They Work? Journal of Marketing, 61(4), 16-29. Oxford University Press. (2013). Oxford English Dictionary (OED). Retrieved 12 of February, 2013, from www.oed.com Patton, M. Q. (2002). Qualitative Research & Evaluation Methods: Thousand Oaks, CA: Sage Publications. Peattie, S., & Peattie, K. (2003). Ready to Fly Solo? Reducing Social Marketing's Dependence on Commercial Theory. Marketing Theory, 3(3), 365-385. Petty, R. E., & Cacioppo, J. T. (1986). The elaboration likelihood model of persuasion. In L. Berkowitz (Ed.), Advances in experimental social psychology (Vol. 19, pp. 123-205). New York: Academic Press. Piaget, J. (1952). The Origins of Intelligence in Children. New York: International Universities Press.
  • 240. References 220 Piaget, J. (1969). Mechanisms of perception. (Translation by G.N.Seagrim) New York: Basic Books. Poortinga, W., Pidgeon, N. F., & Lorenzoni, I. (2006). Public Perceptions of Nuclear Power, Climate Change and Energy Options in Britain: Summary Findings of a Survey Conducted during October and November 2005 Technical Report (Understanding Risk Working Paper 06-02). Norwich: Centre for Environmental Risk. Poortinga, W., Steg, L., & Vlek, C. (2004). Values, Environmental Concern, and Environmental Behavior A Study into Household Energy Use. Environment and behavior, 36(1), 70-93. Portuguese Government (2013). Council of Ministers Resolution No 20/2013. The Portuguese Official Gazette Series 1, 70. Poumanyvong, P., & Kaneko, S. (2010). Does urbanization lead to less energy use and lower CO2 emissions? A cross-country analysis. Ecological Economics, 70, 434–444. Powell, R. R. (1997). Basic Research Methods for Librarians: Greenwood Publishing Group. Powell, R., & Single, H. (1996). Focus Groups. International Journal of Quality in Health Care, 8(5), 499-504. Prendergrast, J., Foley, B., Menne, V., & Isaac, A. K. (2008). Creatures of Habit: The Art of Behavioural Change. London, UK: The Social Marketing Foundation. Quercus. (2008). Projecto EcoFamílias – Relatório Final. Quitzau, M-B., & Røpke, I. (2008). The Construction of Normal Expectations. Consumption Drivers for the Danish Bathroom Boom. Journal of Industrial Ecology, 12(2), 186 – 206. Randles, S. (2009). Practice(s) and ratchet(s). a sociological examination of frequent flying. In P. U. Gössling (Ed.), Climate Change and Aviation: Issues, Challenges, and Solutions (pp. 245-272). London: Earthscan Ltd. Reynolds, T. W., Bostrom, A., Read, D., & Morgan, M. G. (2010). Now what do people know about global climate change? Survey studies of educated laypeople. Risk Analysis, 30(10), 1520-1538. Roberts, S., & Baker, W. (2003). Towards effective energy information. Improving consumer feedback on energy consumption. A report to OFGEM. http://www.cse.org.uk/pdf/pub1014.pdf Rohan, M. J. (2000). A rose by any name? The values construct. Personality and social psychology review, 4(3), 255-277. Rossini, Giuliana, 2009. “Hydro One: In Home Real Time Display: Customer Feedback from a 30,000 Unit Deployment”. Home Energy Displays Conference, Orlando, 2 April 2009 Rotter, J. B. (1954). Social learning and clinical psychology, Englewood Cliffs: Prentice-Hall. Royal Society of London, & U.S. National Academy of Sciences. (1997). Towards Sustainable Consumption. Population and Development Review, 23(3), 683-686. Rudestam, Kjell Erik & Newton, Rae R. (2001). Surviving Your Dissertation: A Comprehensive Guide to Content and Process, London: SAGE Publications. Schiffman, Leon, & Kanuk, Leslie. (1999). Consumer Behavior: Prentice Hall. Schipper, L., & Grubb, M. (2000). On the rebound? Feedback between energy intensities and energy uses in IEA countries. Energy Policy, 28(6-7), 367–388. Schultz, P. W. (2002). Knowledge, Information, and Household Recycling: Examining the Knowledge-Deficit Model of Behavior Change. In T. Dietz & P. C. Stern (Eds.), New tools for environmental protection: education, information, and voluntary measures (1st ed., pp. 67-82). Washington DC: National Academies Press.
  • 241. References 221 Schultz, P. W., Gouveia, V. V., Cameron, L. D., Tankha, G., Schmuck, P., & Franěk, M. (2005). Values and their relationship to environmental concern and conservation behavior. Journal of cross-cultural psychology, 36(4), 457-475. Schultz, P. W., Nola, J. M., Cialdini, R. B., Goldstein, N. J., & Griskevicius, V. (2007). The Constructive, Destructive, and Reconstructive Power of Social Norms. Psychological Science, 18(5), 429-434. Schultz, P. W., Oskamp, S., & Mainieri, T. (1995). Who recycles and when? A review of personal and situational factors. Journal of Environmental Psychology, 15(2), 105-121. Schwartz, B. (in Hastings, G. (2008). Social Marketing: Why should the devil have all the best tunes? Butterworth Heinemann. Schwartz, S. H. (1970). Elicitation of moral obligation and self-sacrificing behavior. Journal of Personality and Social Psychology, 15, 283-293. Schwartz, S. H. (1977). Normative influences on altruism. In L. Berkowitz (Ed.), Advances in experimental social psychology (Vol. 10, pp. 221-279). San Diego, CA: Academic Press. Schwartz, S. H. (1992). Universals in the content and structure of values: Theory and empirical tests in 20 countries. In M. Zanna (Ed.), Advances in experimental social psychology (Vol. 25, pp. 1–65). New York: Academic Press. Schwitzgebel, E. (2010). Acting Contrary to Our Professed Beliefs, or The Gulf Between Occurrent Judgment and Dispositional Belief. Pacific Philosophical Quarterly, 91, 531-553. Scottish Government. (2010). Summary of differences in UK Fuel Poverty methodologies. Sedgwick, Peter, & Edgar, Andrew. (1999). Key Concepts in Cultural Theory. London, UK: Routledge. SEI. (2003). A Review of Fuel Poverty and Low Income Housing (pp. 72). Ireland: Sustainable Energy Ireland (SEI). Sherif, C. W., Sherif, M., & Nebergall, R. E. (1965). Attitudes and attitude change: The social judgment- involvement approach. Philadelphia: W. B. Saunders. Sherif, M., & Hovland, C. I. (1961). Social judgment: Assimilation and contrast effects in communication and attitude change. New Haven, CT: Yale University Press. Shome, D., & Marx, S. (2009). The psychology of climate change communication: a guide for scientists, journalists, educators, political aides, and the interested public (A. Cimino & Leapfrog Communications Eds.). New York: The Trustees of Columbia University, Centre for Research on Environmental Decisions. Shove, E. (2003). Converging conventions of comfort, cleanliness and convenience. Journal of Consumer Policy, 26(4), 395-418. Shove, E. (2004). Efficiency and Consumption: Technology and Practice. Energy & Environment, 15(6), 1053- 1065. Shove, E. (2005). Consumption - Perspectives from ecological economics. In Ropke, I. & Reisch, L. (Ed.). Cheltenham: Elgar, p. 111-132 22 p. Shove, E. (2006). Efficiency and consumption: technology and practice. In T. Jackson (Ed.), The Earthscan Reader in Sustainable Consumption. London, Sterling VA: Earthscan. Shove, E. (2009). Habits and their creatures (pp. 3): Department of Sociology, Lancaster University. Shove, E., & Southerton, D. (2000). Defrosting the Freezer: From Novelty to Convenience A Narrative of Normalization. Journal of Material Culture, 5(3), 301-319.
  • 242. References 222 Shove, E.; Chappells, H.; Lutzenhiser, L., & Hackett, B. (2008). Comfort in a lower carbon society. Building Research & Information, 36(4), 307-311. SILC. (2007). Module: Housing conditions. http://epp.eurostat.ec.europa.eu/portal/page/portal/income_social_inclusion_living_conditions/d ata/ad_hoc_modules Simons, H. W. (1976). Persuasion: Understanding, Practice, and Analysis. London, UK: Addison-Wesley Publishing Company. Skinner, B. F. (1971). Beyond freedom and dignity. New York: Alfred A. Knopf. Slovic, P. (2000). The perception of risk. London: Earthscan. Slovic, P., Finucane, M. L., Peters, E., & MacGregor, D. G. (2004). Risk as analysis and risk as feelings: Some thoughts about affect, reason, risk, and rationality. Risk analysis, 24(2), 311-322. Smith, A. (1776). An Inquiry into the Nature and Causes of the Wealth of Nations (E. Cannan Ed.): University Of Chicago Press. Sorrell, S. (2007). The Rebound Effect: an assessment of the evidence for economy-wide energy savings from improved energy efficiency. UK: The UK Energy Research Centre (UKERC). Southerton, D., McMeekin, A., & Evans, D. (2011). International Review of Behaviour Change Initiatives Retrieved from www.scotland.gov.uk/socialresearch Spaargaren, G., & van Vliet, B. (2000). Lifestyle, Consumption and the Environment: the ecological modernisation of domestic consumption. Society and Natural Resources, 9, 50-76. Staats, H., Harland, P., & Wilke, H. A. (2004). Effecting durable change a team approach to improve environmental behavior in the household. Environment and Behavior, 36(3), 341-367. Staats, H. J., Wit, A. P., & Midden, C. Y. H. (1996). Communicating the greenhouse effect to the public: Evaluation of a mass media campaign from a social dilemma perspective. Journal of Environmental Management, 45, 189–203. Staats, H., Leeuwen, E., & Wit, A. (2000). A longitudinal study of informational interventions to save energy in an office building. Journal of Applied Behavior Analysis, 33(1), 101-104. Stake, R. (1995). The art of case study research. Thousand Oaks, CA: Sage Publications. Steg, L. (2003). Can public transport compete with the private car. IATSS Research, 27(2), 27–35. Steg, L., Dreijerink, L., & Abrahamse, W. . (2006). Acceptability of Energy Policies. Environment and Behavior, 38, 92-111. Stern, N. (2007). The Economics of Climate Change: The Stern Review: Cambridge University Press. Stern, P. C. (1992). What psychology knows about energy conservation. American Psychologist, 47(10), 1224-1232. Stern, P. C. (1997). Toward a working definition of consumption for environmental research and policy. In P. C. Stern, T. Dietz, V. R. Ruttan, R. H. Socolow, & J. L. Sweeney (Eds.), Environmentally significant consumption: Research directions (pp. 12–35). Washington, DC: National Academy Press, 1997. Stern, P. C. (1999). Information, incentives, and proenvironmental consumer behavior. Journal of Consumer Policy, 22, 461–478. Stern, P. C. (2000). Toward a Coherent Theory of Environmentally Significant Behavior. Journal of Social Issues, 56(3), 407–424.
  • 243. References 223 Stern, P. C., Dietz, T., Kalof, L., & Guagnano, G. A. (1995). Values, beliefs, and pro-environmental action: attitude formation toward emergent attitude objects. Journal of Applied Social Psychology, 25, 1611-1636. Stevensen, F, & Rijal, H. B. (2010). Developing occupancy feedback from a prototype to improve housing production. Building Research & Information, 35 (5), 549-563. Streimikiene, D. (2012). The impact of intervention measures on household energy conservation and the GHG emission reduction in Lithuania. Intellectual Economics, 6(1 (13)), 713-729. Streimikiene, D., & Ciegis, R. (2010). The Changes of Life Style: Significant Contribution to GHG emission Reduction Efforts. In W. L. Filho (Ed.), Universities for Climate Change (pp. 280-299). Berlin: Springer-Verlag. Strengers, Y. (2008). Comfort expectations: the impact of demand-management strategies in Australia, Building Research & Information, 36 (4), 381-391. Tabara, D., Darier, E., Gerger, A., Kasemir, B., Schule, R., 1999. Knowledge for sustainability: reflexive learning and mass communication on Global Environmental Change. Paper based on research carried out under the ULYSSES Project, financed by DG XII of the European Commission. Tashakkori, A., & Teddlie, C. (2010). Handbook of mixed methods in social & behavioral research (pp. 189- 208). London: Sage Publications. Thaler, R. H. (1981). Some empirical evidence on dynamic inconsistency. Economics Letters, 8(3), 201-207. Thaler, R. H., & Sunstein, C. R. (2008). Nudge: Improving decisions about health, wealth, and happiness: Yale University Press. The Royal Society. (2012). People and the planet, summary and recommendations. London, UK: The Royal Society Science Policy Centre, Excellence in Science. The University of York. (n.d.). EU Fuel Poverty Network. http://fuelpoverty.eu/ Thøgersen, J. (2005). How may consumer policy empower consumers for sustainable lifestyles. Journal of Consumer Policy, 18, 143-178. Thøgersen, J., & Møller, B. (2008). Breaking car use habits: The effectiveness of a free one-month travelcard. Transportation, 35(3), 329-345. Thøgersen, John. (2004). A cognitive dissonance interpretation of consistencies and inconsistencies in environmentally responsible behavior. Journal of Environmental Psychology, 24(1), 93-103. Thøgersen, John, & Ølander, Carl Folke. (2002). Human values and the emergence of a sustainable consumption pattern: A panel study. Journal of Economic Psychology, 23(5), 605-630. Thomas, C., & Sharp, V. (2013). Understanding the normalisation of recycling behaviour and its implications for other pro-environmental behaviours: a review of social norms and recycling. Resources, Conservation and Recycling, 79, 11–20. Throne-Holst, H., Strandbakken, P., & Stø, E. (2008). Identification of households' barriers to energy saving solutions. Management of Environmental Quality: An International Journal, 19(1), 54 - 66. Tobler, C., Visschers, V. H., & Siegrist, M. . (2012). Addressing climate change: Determinants of consumers' willingness to act and to support policy measures. Journal of Environmental Psychology, 32(3), 197- 207. Townsend, P. (1979). Poverty in the United Kingdom. London, UK: Allen Lane and Penguin Books. Triandis, H. (1977). Interpersonal Behaviour. Monterey, CA: Brooks/Cole.
  • 244. References 224 Tversky, A., & Kahneman, D. (1991). Loss aversion in riskless choice: a reference dependent model. Quarterly journal of economics, 106, 1039-1061. U.S. Census Bureau. (2011). International Data Base. In U. S. D. o. C. United States Census Bureau (Ed.). UK Government. (2013). Fuel Poverty Statistics. https://www.gov.uk/government/organisations/department-of-energy-climate- change/series/fuel-poverty-statistics UN. (1987). Report of the World Commission on Environment and Development: Our Common Future. Transmitted to the General Assembly as an Annex to document A/42/427 - Development and International Co-operation: Environment. http://www.un-documents.net/wced-ocf.htm UN. (1992). Agenda 21 Rio declaration Retrieved from http://www.un-documents.net/agenda21.htm UN. (2007). World Population Prospects, The 2006 Revision, Highlights. New York: Department of Economic and Social Affairs, Population Division. UN. (2011). File 1: Total population (both sexes combined) by major area, region and country, annually for 1950-2100 (thousands): United Nations (UN), Department of Economic and Social Affairs, Population Division. Upham, P., Whitmarsh, L., Poortinga, W., Purdam, K., Darnton, A., McLachlan, C., & Devine-Wright, P. (2009). Public Attitudes to Environmental Change: a selective review of theory and practice. Manchester, UK: ESRC/LWEC. Uusitalo, L. (1990). Are Environment Attitude and Behaviour Inconsistent? Finding from a Finnish Study. Scandinavian Political Studies, 13(2), 211-226. van der Pligt, J. (1985). Energy conservation: two easy ways out. Journal of Applied Social Psychology Bulletin, 15(1), 3-15. Vandenbergh, M., Barkenbus, J., & Gilligan, J. (2008). Individual carbon emissions: The low-hanging fruit. UCLA Law Review, 55, 8-36. Verplanken, B., & Faes, S. (1999). Good intentions, bad habits, and effects of forming implementation intentions on healthy eating. European Journal of Social Psychology, 29(5-6), 591-604. Verplanken, B., & Holland, R. (2002). Motivated decision making: Effects of activation and self-centrality of values on choices and behavior. Journal of Personality and Social Psychology, 82, 434-447. Vygotsky, L S (1978) “Mind and Society: the Development of Higher Psychological Processes”, Harvard University Press, Cambridge. MA. Wackernagel, M., Schulz, B., Deumling, D., Callejas Linares, A., Jenkins, M., Kapos, V., Randers, J. (2002). Tracking the ecological overshoot of the human economy. Proceedings of the National Academy of Sciences of the United States of America, 99(14), 9266-9271. Weaver, K., & Olson, J. K. (2006). Understanding paradigms used for nursing research. Journal of Advanced Nursing, 53(4), 459-469 Weber, E. U. (1997). Perception and expectation of climate change: Precondition for economic and technological adaptation. In M. Bazerman, D. Messick, A. Tenbrunsel & K. Wade-Benzoni (Eds.), Psychological and Ethical Perspectives to Environmental and Ethical Issues in Management (pp. 314-341). San Francisco: Jossey-Bass. Weber, E. U. (2006). Evidence-based and description-based perceptions of long-term risk: Why global warming does not scare us (yet). Climatic Change, 77, 103-120. Weinreich, N. K. (1999). Hands on social marketing: A step by step guide. Thousand Oaks, CA: Sage.
  • 245. References 225 Whitmarsh, L. E. (2009). Social and psychological drivers of energy consumption behaviour and energy transitions. In S. Dietz, J. Michie & C. Oughton (Eds.), Political Economy of the Environment: An Interdisciplinary Approach (pp. 213-228): Taylor & Francis. Whitmarsh, L. E., Turnpenny, J., & Nykvist, B. (2009). Beyond the regime: can Integrated Sustainability Assessment address the barriers to effective sustainable passenger mobility policy? Journal of Environmental Planning and Management, 52(8), 973-991. Wilhite, H., & Lutzenhiser, L. (1999). Social Loading and Sustainable Consumption. In E. J. Arnould & L. M. Scott (Eds.), NA - Advances in Consumer Research (Vol. 26, pp. 281-287). Provo, UT: Association for Consumer Research. Wilhite, H. & Richard, L. (1992). "The Person Behind the Meter: An Ethnographic Analysis of Residential Energy Consumption in Oslo, Norway." Proceedings from the ACEEE 1992 Summer Study on Energy Efficiency in Buildings 10:177-186. Washington, D. C.: ACEEE Press. Wilkinson, D., & Birmingham, P. (2003). Using Research Instruments: a guide for researchers. London, UK: Routledge. Williamson, T.; Soebarto, V. & Radford, A. (2010). Comfort and energy use in five Australian award-winning houses: regulated, measured and perceived, Building Research & Information, 38(5), 509-529. Winett, R. A., & Kagel, J. H. (1984). Effects of information presentation format on resource use in field studies. Journal of Consumer Research, 11, 655–667. Winett, R. A., Leckliter, I. N., Chinn, D. E., Stahl, B., & Love, S. Q. (1985). Effects of television modeling on residential energy conservation. Journal of Applied Behavior Analysis, 18, 33–44. Winter, D. D. N. , & Koger, S. M. (2004). The Psychology of Environmental Problems: Lawrence Erlbaum. Wright, A. (2008). What is the relationship between built form and energy use in dwellings? Energy Policy, 36(12), 4544-4547. WHO. (2012). Environmental health inequalities in Europe. Copenhagen, Denmark: World Health Organization (WHO). WWF. (2008). Living Planet report 2008: World Wide Fund for Nature (WWF). WWF. (2012). Living Planet report 2012 - Biodiversity, biocapacity and better choices: World Wide Fund for Nature (WWF).
  • 255. Appendices 235 Appendix III: Consumer interview roadmap 1. How easy or difficult do you find to reduce the amount of energy you use at home on a day to day base? a. Follow up question: what are the reasons for easiness or difficultness? b. Follow up question: if you would need to chose one reason from all the above for easiness or difficultness which one would it be? c. Back up information: list of barriers from FG: i. Comfort ii. Habits iii. Willingness/Laziness/resistance to change iv. Self-indulgence v. Environment/future vi. Initial investment/RoI vii. Information viii. Actions already taken ix. Economical conditions x. Social norms, social dilemma and hypocrisy 2. What does comfort mean to you at home? How does it affect your day to day use of energy? Can you provide some examples? a. Prompt for thermal comfort b. Prompt for showering habits c. Prompt for lighting practices d. Prompt for having the TV on even if not watching e. Prompt for leaving stand-by on f. Prompt for using appliances such as washing machines at any point of the day g. Prompt for leaving fridge open 3. Can you describe your expectations of a minimum level of comfort at home? 4. If you had to chose between spending less on energy and maintaining your comfort level, what would you chose? a. At which point would your priorities change? b. What could trigger change? c. Have you ever been at a situation were you needed to reduce your comfort level? Can you describe the circumstances?
  • 256. Appendices 236 5. Some people have been referring to the fact that changing some of their behaviours might be quite inconvenient/you have mentioned the fact that changing some of those behaviours would be quite inconvenient to you. Is comfort and convenience the same to you? What are the similarities/differences between the two of them? a. Prompt for standby b. Prompt for off peak tariffs c. Prompt for leaving the door of the fridge opne/open frequently d. Prompt for cooking with lids on 6. Which actions could you take in order to reduce your energy bill without reducing your comfort level? (Write in a paper) a. Follow up: can you please order the actions you just mentioned, starting with the one you would do first to the one you would do the last (use the paper from above) b. Follow up question: Can you develop on the reasoning of the ordering? 7. How do you consider your energy use level at home? High, normal, average, low or conditioned? a. Can you explain the reasons for locating yourself as XXX? b. What is for you a ‘normal’ energy use level? c. How would you describe it? d. What about your family and friends? How do you perceive their energy use to be? e. Where do you locate yourself within this graph?
  • 258. Appendices 238 Appendix IV: Practitioner interview roadmap 1. How easy or difficult do you think it is for people to reduce their energy use at home ? a. How do you understand the easiness to change one time investment decisions? b. How do you understand the easiness to change daily habitual behaviours? 2. Which barriers to change do people face in reducing their energy use with regards to changing their daily habitual behaviours? a. Backup information: i. Lack of information ii. Lack of financial resources iii. Resistance to change iv. Ingrained habits v. Lack of motivation vi. Lack of environmental concerns vii. Lack of connection between their individual energy use to the global consumption viii. Locked to building infrastructure ix. Limited by other family members x. Unwillingness to reduce comfort level xi. Convenience of current behaviours 3. From the barriers you mentioned, which do you identify as important once designing interventions and why? a. Can you recall an example when that was done? b. Have those interventions been effective? c. How do you know that? d. Has your organization focused their interventions on any of those barriers you just mentioned as important? If not, what could be the reason for such? If yes, how successful have they been? e. How do you perceive that people receive and enrol on initiatives to promote less energy intensive lifestyles 4. You have been mentioning/people have been mentioning that maintaining comfort level is quite important for them. What do you think people mean by comfort? a. What is your understanding of the role of comfort as a barrier to change individual energy use? b. Has your organization ever tried to tackle the existing expectation for comfort within their interventions? c. How do you think comfort should be included within future interventions? d. Do you think it would be feasible to promote an adaptation of the level of individual comfort?
  • 259. Appendices 239 e. How would you communicate the need to reduce comfort in a world that might run out of energy, how would you disrupt the flow of current messages and set a different agenda? 5. You have been mentioning/people have been mentioning that changing their daily behaviours is inconvenient. What do you think people mean by convenience? a. What is your understanding of the role of convenience as a barrier to change individual energy use? b. Has your organization ever tried to tackle the existing expectation for convenience within their interventions? c. How do you think convenience should be included within future interventions? d. Do you think it would be feasible to promote an adaptation of the level of convenience of current behaviours? 6. In your opinion, what does ‘normal’ energy consumption means to individual users or households? KWh, cost or services? a. How do you consider individual users are influenced by what they see as normal? b. How could one influence this idea of ‘normal’ consumption? c. Has your organization ever tried to tackle the existing norms within their interventions? d. How do you think norms should be included within future interventions? e. How would you communicate the need to change norms? f. Do you believe norms could be changed through a carrot and stick approach? g. Do you think it would be feasible to promote an adaptation of norms?
  • 260. Appendices 240 Appendix V: List of answers for Question 6 of EP survey questionnaire regarding energy saving reported behaviours
  • 263. Appendices 243 Appendix VIII: – List of answers for question Q16 of EP survey questionnaire (reported barriers and constraints) 0,0% 10,0% 20,0% 30,0% 40,0% 50,0% 60,0% Already do what I can I save enough already/I save too much already I would like to do more, but don’t know how It would reduce my comfort I don’t have time to do more/I’m too busy I don’t want to know/it doesn’t concern me It’s not useful/it’s not necessary It would be very expensive The greatest polluter is the industry It wouldn’t make any difference I don’t see any reduction in the bill Alone it wouldn’t make any difference/I do it … The future will come up with solutions Electricity/gas is cheap / I pay very little 50,3% 22,1% 16,9% 10,6% 8,2% 3,9% 2,3% 1,7% 1,4% 1,4% 0,9% 0,9% 0,8% 0,2% Reported barriers to save energy (in %)
  • 265. Appendices 245 Appendix X: – Sample distribution with regard to region, gender, age groups and rural/urban area Male Female 16-25 years 25-45 years >45 years 16-25 years 25-45 years >45 years Total North URBAN 14 15 14 14 14 14 85 170 (16.7%) RURAL 14 14 14 14 15 14 85 Centre URBAN 14 14 14 14 15 15 86 172 (16.9%) RURAL 14 14 14 15 14 15 86 Lisboa URBAN 12 16 12 14 16 9 79 164 (16.1%) RURAL 14 14 14 14 15 14 85 Alentejo URBAN 14 14 14 14 14 14 84 170 (16.7%) RURAL 14 14 14 15 14 15 86 Algarve URBAN 14 14 14 14 14 14 84 170 (16.7%) RURAL 15 15 14 14 14 14 86 Islands URBAN 14 14 14 14 14 15 85 173 (17%) RURAL 14 15 14 15 15 15 88 167 173 166 171 174 168 1.019