Investigation & Examination of Noise Pollution - Definition, Sources, Effects, Monitoring and Control
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1. Introduction
The word ‘Noise’ is originated from the Latin word “nausea” implying – ‘Unpleasant
Sound’, Unwanted Sound’, ‘Sound that is loud’, ‘A Harsh Sound, and ‘Sound that is
unexpected’. A sound becomes noise when it is unpleasant, unwanted, loud and
unexpected and detrimental physiological and psychological effect on human. A sound can
be unpleasant due to intensity of sound, time of exposure, continuity of sound and its
frequency. In general, noise is any sound that humans do not want to hear. Noise is one of
the environmental pollution that affects the quality of life of particularly of population at
urban areas worldwide. It has increased in the modern age of industrialization and
technological advancement. According to recent publication by the World Health
Organization (WHO, 2018) at least 100 million people are affected by road noise in the
European Union and at least 1.6 million years of healthy life are lost every year. In such
noisy urban areas, people seem to have become accustomed to the higher noise levels.
According to European Commission (1996), it is affecting human behaviour, well-being,
productivity and health. Urbanization, economic growth and motorized transport are some
of the driving forces for environmental noise exposure and adverse health effects. In India,
noise is one of the most pervasive pollutant and growing problem because Indian people
generally have traditional liking for noise, consequently noise is often regarded with the
lowest priority for control and management. Most of our happy and sad moments of life
are expressed through noise. It may be in the form of busting of crackers, playing loud
music in parties and marriages, recitation of religious scriptures and hooting in events etc.
Thus there is a silent compromise by us to take noise as a normal part of our routine life
without realizing its adverse effects on our life and health. That is the one of main reason
that the movement against noise pollution is weak in India. The health impacts of
environmental noise are a growing concern among both the general public and policy-
makers in India. Currently, limited research studies exist on the exposure-effect-response
of noise and its sources & controls in the Indian scenario. In view of this, the present
research has been carried out in metro city Delhi of India to synthesize noise definition,
empirically investigating public reactions towards sources of noise, noise-induced-effect-
response of public and control of noise.
2. Purpose
Aiming at studying the noise pollution for its definition, sources, effects and control;
this study has following research objectives:-
a. Understanding and definition of noise in respect of environmental pollution.
b. Exploring the indoor and outdoor sources of noise pollution
c. To investigate the awareness level of public.
d. To investigate the public reactions on sources of noise.
e. To examine the public reactions on noise induced health impacts.
f. To explore the solutions to control the noise.
3. Understanding and Definition of Noise
Synthesis of noise is carried out to arrive at a most appropriate definition of noise.
Noise is a “sound without value” or “any noise that is unwanted by the recipient”. The
loudness of noise varies from person to person so no precision definition is possible.
Sound/noise is measured in dB (Decibel). The difference between sound and noise are
often subjective and is a matter of personal opinion, however author has attempted to
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explain this difference with the help of Figure-1. Sound (or noise) is the result of pressure
variations, or oscillations, in an elastic medium (e.g., air, water, solids), generated by a
vibrating surface, or turbulent fluid flow. Sound propagates in the form of longitudinal (as
opposed to transverse) waves, involving a succession of compressions and rarefactions in
the elastic medium. Sound becomes noise when the three elements (as shown in Figure-1)
(i) Sound Pattern, (ii) Sound Intensity and (iii) exposure duration are having values other
than specified norms. The general perception of sound in term of intensity of loudness (dB)
is provided in Figure-2 and general noise exposure limits are shown in Figure-3. What is
pleasant to some ears may be extremely unpleasant to others depending up on number of
psychological factors.
Figure -1 : Understanding Noise
Source:- Authors’ creation
Singh, K.P and Singha, S. (1983) defined noise as a type of atmospheric pollution in
the form of waves. It is a shadowy public enemy. According to encyclopedia Britainica
(1968), noise is defined as any undesired sound in acoustics. Usually, noise is a mixture of
many tones combined in a non-musical manner. According to encyclopedia Americana
(1968), noise is defined as unwanted sound. The sweetest music, if it disturbs a person who
is trying to concentrate or to sleep, is a noise to him, just as the sound of a pneumatic
riveting hammer is noise to nearly everyone. In other words, any sound may be noise if
circumstances cause it to be disturbing. In its guidelines for community noise (1999), the
WHO defined environmental noise as “noise emitted from all sources except for noise at
the industrial workplace”. European Union (EU) Directive 2002/49/EC on the management
of environmental noise (2002) defined environmental noise as “unwanted or harmful
outdoor sound created by human activities, including noise from road, rail, airports and
from industrial sites”. W. W. Seto (1971) and B.G. Liptak et al. (1997) also argued that
noise is simply anything that we hear and is subjectively defined as unpleasant or
unwanted sound. Consequently, a sound can be noise to one person and not to others, or
noise at one time and not at other times. So we can say that sound loud enough to be
harmful is called noise without regard to its other characteristics. According to
Environmental Health Criteria-126 'noise is considered as any unwanted sound that may
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adversely affect the health and well-being of individuals or the populations'. H. S. Bhatia
(1998) defined noise as any sound independent of loudness that can produce an undesired
physiological or psychological effect in an individual and that may interfere with the social
ends of an individual or group. These social ends include all of our activities like
communication, work, and sleep etc. The Wilson committee of Britain (1963) defined
noise as sound which is undesired by the recipient.
Figure -2 : Perception level of sound Figure -3 : Noise exposure limits
Source:- Compilation by Authors Source:- Compilation by Authors
Therefore, in this study, we can arrive at following most appropriate definition of
noise in respect of ambient air quality:-
“Noise, in context of environmental pollution, is an unpleasant & unwanted
excessive sound (or combination of sounds) above than specified limits [dB(A)] in
a particular area emitted from any source; which is undesired & disagreeable to
the recipient due to ‘adverse effects on his health’ like damage to hearing, disrupt
sleep, hypertension, high blood pressure, cognitive impairment & other diseases
and ‘bad effects on his routine life’ like annoyance, discomfort, interference with
speech & communication, reduction in efficiency of work performance &
disturbance to his normal activities.”
4. Literature Review
4.1 Sources of Noise Pollution
There is a need to first identify sources of noise to deal effectively with problem of
noise. In India, the increasing ambient noise levels in public places are resulted from
various sources like industrial activity, construction activity, fire crackers, sound producing
instruments, generator sets, loud speakers, public address systems, music systems,
vehicular horns, other mechanical devices, stone crushing machine, defence equipment,
television, refrigerator, air conditioners and other home appliances etc.
As shown in Figure-4, all these sources of noise pollution can be broadly categories as
indoor and outdoor noise pollutants. The indoor noise pollutants are associated with human
activities within the building, operation of building services and office equipment. These
may include door slam, footfall (especially in multi-story buildings), conversation, radio
and television sets, fans and air-conditioners, home appliances and motorized appliances
such as power generating sets (Ogunsote, 2010). Outdoor noise pollutants constitute the
major sources of environmental noise. The noise caused by outdoor pollutants may be
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difficult to control from the source. They include, but are not limited to the following:-
noise from traffic and automobiles; noise from industries like quarries and mining
industries; noise from pedestrians; noise from religious institutions like churches and
mosques; noise from advertising agents and hawkers; noise from rallies like political
campaigns, and so on (Ogunsote, 2010).
Figure - 4 : Various Indoor and Outdoor Noise Pollutants
Source: Authors’ compilation
Further population, unawareness about harmful effects of noise pollution,
industrialization advancement and advance motorized transport are some of the major
contributors for environmental noise. Day & night, a large number of cars, trucks,
motorcycles, air-flights and other motorized vehicles criss-cross the cities and resulting
noise pollution.
Table-1 : Typical sound levels encountered in daily life and industry
Activity Sound
Level
dB(A)
Graphical scale of sound level in respects of
transport oriented sound levels
Desert 10
Rustling Leaves 20
Room in a quiet dwelling at midnight 32
Soft whispers at 5 feet 34
Men’s clothing department of large store 53
Window air conditioner 55
Conversational Speech 60
Household department of large store 62
Busy restaurant 65
Vacuum cleaner in private residence 69
Ringing alarm clock at 2 feet 80
Loudly reproduced orchestral music 82
Prolonged exposure - hearing damage 85
Lorry or motorbike close by 90
Rock concert , loud disco 100
Pneumatic Drill 110
Jet aircraft take-off 130
Gunshots, explosions 140
Source: Tam 2000 Source :World Bank, 1997
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According to Birgitta and Lindvall (1995), road traffic, jet planes, garbage trucks,
construction equipment, manufacturing processes, and lawn mowers are some of the major
sources of this unwanted sounds that are routinely broadcasted into the air. Ritovska et al.,
(2004) also emphasized that improper use of horn by the traffic and wide use of
loudspeakers in Indian religious and social ceremonies are major noise pollutants causing
health risk to human. As per Goines and Hagler (2007), noise is a major environmental risk
of the global world, originating from a different variety of sources including traffic, which
plays main role in noise pollution. It is important to have an understanding of sound levels
we typically encountered in our daily routine life. Table-1 provides a list of sound levels
from typical situations along with a graphic scale of transport oriented sound levels.
4.2 Effects of Noise Pollution
Noise impacts health. The role of noise as an environmental pollutant and its impact on
health are being increasingly recognized. The effect of noise on any human being may be
psychological or physiological (Ogunsote, 2010; Adedeji and Folorunsho, 2010).
Generally, sound is considered as noise pollutant having intensity more than 60 dB.
Environmental noise is a psycho-social stressor that affects subjective well-being and
physical health (WHO 1999; van Kamp I et. al 2012; EPoN 2010). Noise degrades
environment and also causes health hazard to human beings. Exposure to noise for a
continuous period of time will have many serious health issues, which may be temporary
or permanent. Table-2 provides the details of different sound levels and their harmful
effects. Even relatively low levels of noise affect human health adversely (Kiernan, 1997).
It may cause hypertension, hearing loss, sleep disruption, cognitive impairment in children,
tinnitus, reduced productivity, absenteeism and accidents, cardiovascular disease,
annoyance & frustration reactions, social handicaps, negative social behaviour, high blood
pressure, anxiety & stress related illness, memory loss, severe depression, and panic
attacks.
Table-2 : Different sound levels and harmful effects
Noise level
(dBA)
Possible psychological and physiological effects.
65 Annoyance, mental and physical fatigue.
90 Very long exposure may cause permanent hearing loss.
100 Short exposure may cause temporary damage; long exposure may cause
permanent damage.
120 Pain.
150 Immediate loss of hearing.
Source: : Ogunsote (1991)
Epidemiological studies on the relationship between transportation noise (particularly
road traffic and aircraft noise) and cardiovascular effects have been carried out on adults
and on children. Both road traffic noise and aircraft noise increase the risk of high blood
pressure. At the same equivalent noise level, annoyance and self-reported sleep disturbance
are usually highest for aircraft noise, and higher for road compared with rail traffic noise
(Miedema and Oudcshoorn, 2001). Bond (1996) revealed that the effects of excessive
noise could be so severe that either there is a permanent loss of memory or a psychiatric
disorder .It disturbs and interferes with activities of the individual, including concentration,
communication, relaxation and sleep. Children may be exposed to noise for many of their
childhood years and the consequences of long-term noise exposure on reading
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comprehension and further cognitive development remain unknown. Many studies have
shown negative effects of noise on reading and memory in children (Evans GW, Hygge S,
2007; Evans GW, Lepore SJ, 1993). Tasks affected are those involving central processing
and language, such as reading comprehension, memory and attention (Haines MM et al.
2007). A study in London found that 340 children are exposed to the air craft noise of ages
8-11 resulting in annoyance, poor reading and comprehension (Hagler, 1999). In another
research, children who were exposure to noise levels above 55 dB they have low attention,
less social adaptability, and have opposite behaviour to others compared to children (Costa
et al., 2013). Therefore exposure during critical periods of learning at school could
potentially impair development and have a lifelong effect on educational attainment.
Noise disturbs communication, concentration, relaxation and sleep. Chronic long-term
exposure to transportation noise has been shown to be associated with the prevalence and
incidence of cardiovascular diseases, including hypertension, ischemic heart diseases and
stroke (Babisch W, 2014). Large scale epidemiological studies have been carried out for a
long time (Babisch, 2000). Figure-5 shows a proposed reaction scheme for the effects of
noise on the organism (Babisch W, 2002).
Figure-5 : Noise effects reaction scheme
Source: Adopted from Babisch W (2002), Authors’ re-creation
Sufficient undisturbed sleep is necessary to maintain performance during the day as
well as for general good health (Banks S, Dinges DF, 2007). The human organism
recognizes, evaluates and reacts to environmental sounds even while asleep (Oswald I et
al., 2007). Environmental noise may badly affect the restorative ability of sleep by means
of repeatedly exposure to disrupt sleep due to noise. The repeatedly acute and chronic
sleep disturbance due to noise may further affect other things like energy of body to
perform various tasks, ability to receive and understand other’s communication, signal
detection ability, memory consolidation, creativity, risk taking ability and risk of accidents.
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Another noise induced bad effect on health is tinnitus. To put it in terms of auditory
abilities, tinnitus is the inability to perceive silence (Leroux T, Lalonde M., 1993). Thus
tinnitus is the general term for sound perception (for instance, roaring, hissing or ringing)
that cannot be attributed to an external sound source. It is widely believed that mild,
occasional or acute temporary tinnitus is experienced by nearly everybody in their lifetime
at some time or another (MacFadden D., 1982). The severity of health effects due to noise
versus the number of people affected is schematically presented by Figure-6.
Figure-6 : Severity of health effects of noise and number of people affected
Source: Babisch
Based on the systematic review of evidence produced by epidemiological and
experimental studies, the relationship between night noise exposure and health effects can
be summarized as below (Table -3).
Table-3 : Effects of different levels of night noise on the population’s health
Average night
noise Health effects
observed in the
population level
over a year
Lnight,outside
Health effects observed in the population
(Note. The guidelines assume an average attenuation of 21 dB(A)
between inside and outside noise levels.)
Up to 30 dB Although individual sensitivities and circumstances may differ, it
appears that up to this level no substantial biological effects are
observed. Lnight,outside of 30 dB is equivalent to the no observed effect
level (NOEL) for night noise.
30 to 40 dB A number of effects on sleep are observed from this range: body
movements, awakening, self-reported sleep disturbance, arousals. The
intensity of the effect depends on the nature of the source and the
number of events. Vulnerable groups (for example children, the
chronically ill and the elderly) are more susceptible. However, even in
the worst cases the effects seem modest. Lnight,outside of 40 dB is
equivalent to the lowest observed adverse effect level (LOAEL) for
night noise
40 to 55 dB Adverse health effects are observed among the exposed population.
Many people have to adapt their lives to cope with the noise at night.
Vulnerable groups are more severely affected.
Above 55 dB The situation is considered increasingly dangerous for public health.
Adverse health effects occur frequently, a sizeable proportion of the
population is highly annoyed and sleep-disturbed. There is evidence
that the risk of cardiovascular disease increases.
Source: Night noise guidelines for Europe (38).
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From above literature review, it is evident that noise pollution results many bad effects
on human health and it is therefore of utmost importance to take practical action to limit
and control excessive environmental noise.
4.3 Controls of Noise Pollution
It is considered necessary to regulate and control the noise producing and generating
sources with the objective of maintaining the ambient air quality standards in respect of
noise. In India, the Noise Pollution (Regulation and Control) Rules, 2000 have been
framed under the Environment (Protection) Act, 1986. These are a set of guidelines with
the standard prescribed limits for regulation and control of noise. The ambient levels of
noise for different areas / zones specified in the rules are indicated in Table-4.
Table-4 : Ambient air quality standards in respect of noise
Area Code Category of Area/ Zone Limits in dB*
Day Time Night Time
(A) Industrial Area 75 70
(B) Commercial Area 65 55
(C) Residential Area 55 45
(D) Silence Zone 50 40
Source: Environment (Protection) Act, 1986 as amended in 2002.
Notes regarding Table-4 :-
*The limit in dB denotes the time-weighted average of the level of sound in decibels on Scale A which is
relatable to human hearing.
1. Day time shall mean from 6.00 a.m. to 10.00 p.m.
2. Night time shall mean from 10.00 p.m. to 6.00 a.m.
3. Silence zone is an area comprising not less than 100 meters around hospitals, educational
institutions, courts, religious places or any other area which is declared as such by competent
authority.
4. Mixed categories of areas may be declared as one of the four above mentioned categories by
competent authority.
The Central Pollution Control Board (CPCB) has the responsibility to regulate and
control sources of Noise Pollution with the objective of maintaining the ambient air quality
standards. From above literature review it is observed that experimental knowledge related
to noise is available in literature but less research studies were found based on interaction
with real life and practical world like how noise pollution is understood by human/public,
how much knowledgeable they are for its harmful effects and what they are doing to
reduce and control it. To fill gap, author has tried to attempt this study.
5. Research Methodology
5.1 Location
Location is very important factor for this study. Many researches have indicated high
levels of sound pollution in different urban areas. Delhi is the capital city of India and is
regarded as the heart of the nation. Delhi's urban area is now considered to extend beyond
the NCT (National Capital Territory of Delhi) boundaries, and include the neighbouring
satellite cities of Ghaziabad, Faridabad, Gurgaon and Noida in an area now called National
Capital Region (NCR) and had an estimated population of over 26 million people, making
it the world's second-largest urban area according to the United Nations (2016). Apart from
country’s largest urban agglomerations, Delhi is an important commercial, transport, and
cultural hub. Therefore Delhi is chosen for this study.
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5.2 Sample, Data and Techniques
This empirical study is based on primary data collected through a structured online
questionnaire. The sample represents a cross-section of different age groups, gender and
educational levels. Total 350 responses were collected. The analysis has been carried out
with the help of ‘percentages technique’ and ‘cross classifications’ in terms of ‘age’ as
well as ‘gender’ on awareness of noise pollution, sources of noise, effects of noise, and
suggestions to control noise.
6. Analysis, Results and Findings
6.1 Respondents Demographics
The study is based on cross-classification in term of age and gender. The demographics
details of respondents are shown in Table-5.
Table-5 : Respondents Demographics
Characteristics Value %age
Total Respondents 350 100%
Gender
Male 199 57%
Female 151 43%
Age-Group
Up to 20 ( Say A1<20 ) 66 19%
20-40 ( Say A220-40 ) 120 34%
40-60 ( Say A340-60 ) 91 26%
Above 60 ( Say A4>60 ) 73 21%
Education
Doctorate 45 13%
Post-Graduation 148 42%
Graduation 126 36%
Diploma 7 2%
Others 24 7%
Source: Authors’ Survey Data
6.2 Awareness about Noise Pollution
6.2.1 In terms of Male and Female
Awareness is major agent which can contribute to control and hence reduce the noise
pollution. The awareness level of respondents based on gender is sown in Figure-6, which
presents the %age of male and female respondents answering questions Q1, Q2, Q3 and
Q4 as Yes/No.
It is evident from Figure-7 that in general, male respondents are more aware about the
noise pollution as compared to female (see % age “Yes” response for MaleQ1-80%, MaleQ2-
43%, MaleQ3-77%, MaleQ4-74%) except MaleQ5-65% where female are more aware;
FemaleQ5-68%. However %age difference in “Yes” responses of male and female is not
significant (e.g. 80-64 = 16%, 43-37 = 6%, 77-70 = 7%, 74-66 = 8%, 68-65 = 3%); which
implies that on an average, the awareness of noise pollution is almost equal among male
and female community. The “No” response of 23% by male community and 30% by
female community against question Q3 implies that almost one third of the community,
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especially in the Indian subcontinent, is not aware that noise can cause any health damages
although environmental noise has severe negative impact on human health. This calls for
implementations of actions and initiatives to spread the awareness among Indian
population about harmful effects of noise pollution. The “No” response of 57% of male
community and 63% of female community towards question Q2 also calls for
dissemination of knowledge of limits of noise level.
Thus, there is less awareness in Indian population regarding noise impacts human
health negatively and hence there is need to increase the awareness about noise pollution
among both male and female for better understanding of noise pollution and hence it’s
monitoring & control.
Figure-7 : Awareness about noise pollution in terms of male and female respondents
Source: Authors’ Work
6.2.2 In terms of different age group
The awareness level of respondents based on age groups is sown in Figure-8, which
presents the %age of various respondents from age groups A1<20, A220-40, A340-60 & A4>60
answering questions Q1, Q2, Q3 and Q4 as Yes/No. The analysis indicates that very large
proportion of population in age group A220-40 (valuing “Yes” as 85%, 55%, 91%, 87% &
74% for all questions Q1,Q2,Q3,Q4 & Q5 respectively) and age group A340-60 (valuing
“Yes” as 89%, 54%, 92%, 88% & 71% for all questions Q1,Q2,Q3,Q4 & Q5 respectively)
are more aware about noise pollution as compared to population in youngest age group of
A1<20 (valuing “Yes” as 53%, 24%, 56%, 53% & 62% for all questions Q1,Q2,Q3,Q4 & Q5
respectively) and oldest age group A4>60 (valuing “Yes” as 47%, 86%, 91%, 87% & 74%
for all questions Q1,Q2,Q3,Q4 & Q5 respectively). The awareness about the most
important question Q3 (Do you know that noise impacts to the human health?) is poor in
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respondents in age group of A1<20 & A4>60 (%age of “Yes” population is A1-56%, A4-41%).
The response against question Q2 implies that significant population in all age groups does
not know the about norms of noise limits in their areas. The above analysis brings out most
important point that noise pollution is increasing day by day due to one of major reason of
lack of awareness of noise pollution and its harmful effects.
Figure-8 : Awareness of noise pollution based on different age groups
Source: Authors’ Work
6.3 Reactions of respondents towards Outdoor Noise Pollutants
6.3.1 In terms of Male and Female
The analysis of impact of outdoor sources of noise pollution on male community and
female community differently is shown in Figure -9. The Figure-8 presents the % age of
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male and female respondents affected by different outdoor sources of noise. There are
significant differences in population (more than 10%) affected by noise generated from
“Loudspeakers” and “Parties, Events & Functions” where male population (70% and
50% respectively) is more affected over the female population (54% and 38%
respectively). In terms of remaining sources of noise, there is no significant difference in
% age (less than 10%) of male population and female population. It implies that other
sources of noise (Traffic, Industrial Manufacturing Noise, Religious Functions,
Commercial Construction Noise and Neighbourhoods) affect equally to male population as
well as female population. Ranking wise, male and female population are highly affected
by (1) Traffic followed in descending order by (2) Loudspeakers, (3) Industrial
Manufacturing (4) Noise, Parties, Events & Functions, (5) Religious Functions, (6)
Commercial Construction Noise and (7) Neighbourhoods.
Thus, “Traffic Volume” expanded by road, rail and air traffic as a noise has gained
wider recognition in terms of increasingly serious risk to human health.
Figure-9 : Impact of various outdoor noise pollutants based on gender
Source: Authors’ Work
6.3.2 In terms of different age group
The Figure-10 presents the % age of respondents of different age groups affected by
different outdoor sources of noise. The analysis indicates that a very large proportion of
respondents (ranging from 79% to 89%) in each age group are being affected by noise
emanating from the “Traffic”. On the other hand, very less proportion of respondents
(ranging from 3% to 26%) in all age groups are affected by “Neighbourhoods”. An almost
equal proportions of respondents (ranging from 41% to 75%) across different age-groups
claim that noise originating from “Loudspeakers” affects them. A relatively small
proportion of respondents (ranging from 10% to 55%) acknowledge adverse effect of noise
generated by “Commercial Construction”. Majority of respondents with little %age
difference across different age groups feel that noise originating from “Religious
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Functions”, “Parties, Events & Functions” and “Industrial manufacturing” affects their
activities.
The highly affected proportion of population due to outdoor noise is from age group
A1<20 followed in descending order by age group A340-60, A220-40 and A4>60. The disturbance of
the community of youngest age group A1<20 at large is obvious due to education/study
period of life. The recognition of harmful effects of outdoor noise by the community of
oldest age group A4>60 at small proportion seems true because till age of 60 years people
normally get affected to maximum extent and thereafter they feel less impact of noise
pollution on their life and health.
This analysis brings out that “Traffic” and “Loudspeakers” act as significant sources
of outdoor noise pollution. Thus population at large in Delhi is becoming victim of noise
pollution mainly originating from “Traffic” and “Loudspeakers”.
Figure-10 : Impact of various outdoor noise pollutants based on different age groups
Source: Authors’ Work
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6.4 Reactions of respondents towards Indoor Noise Pollutants
6.4.1 In terms of Male and Female
Figure-11 presents the %age of male and female respondents affected by different
indoor sources of noise. The analysis indicates that there are no significant differences in
%age of population (all are less than 10%) affected by noise generated from indoor
sources. It implies that all indoor sources of noise affect equally to male population as well
as female population. Ranking wise, male and female population are highly affected by (1)
TV (Television) followed in descending order by (2) Different home appliances, (3) Power
Generators, (4) Air Cooler / Air Conditioners, (5) Family conflict, (6) Refrigerators. An
almost equal %age of male and female population has recognised that noise originating
from “TV (Television)”, and “Different home appliances” affects their activities.
Thus, “TV (Television)”, and “Different home appliances”, as a noise are mostly
considered high serious risk to human health.
Figure-11 : Impact of various indoor noise pollutants based on gender
Source: Authors’ Work
6.4.2 In terms of different age group
The Figure-12 presents the %age of respondents of different age groups affected by
different indoor sources of noise. The analysis indicates that a very large proportion of
respondents in each age group are being affected by noise emanating from the “Different
home appliances” ranging from 33% to 60% and from the “TV (Television)” ranging from
29% to 58%. On the other hand, very less proportion of respondents in all age groups is
affected by “Refrigerators” ranging from 5% to 15% and by “Family conflict” ranging
from 8% to 36%. An almost equal proportions of respondents (ranging from 41% to 75%)
across different age-groups claim that noise originating from “Loudspeakers” affects them.
Majority of respondents with significant %age difference across different age groups feel
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that noise originating from “Power Generators”, and “Air Cooler / Air Conditioners”
affects their activities.
The major proportion of respondents (58%) in youngest age group A1<20 feel that they
are most affected by the noise from “Air Cooler / Air Conditioners” however on other
hand large proportion (60%) of oldest age group A4>60 acknowledge harmful effect due to
“Different home appliance”. Highest proportion of age groups A220-40 (58%) and A340-60
(54%) responded that their life is badly affected by the noise originating from TV
(television). The noise originating from “Refrigerators” is affecting least population in
each age group.
Figure-12 : Impact of various indoor noise pollutants based on different age group
Source: Authors’ Work
Therefore “TV (Television)”, and “Different home appliances”, act as significant
sources of indoor noise pollution and affect each age group differently. Thus, large
population of metropolitan cities is mostly affected by the noise originating from indoor
noise pollutants “TV (Television)”, and “Different home appliances”.
6.5 Reaction of Respondents regarding effect of Noise Pollution
6.5.1 In terms of Male and Female
Figure-13 shows the perception of male and female populations about the effect of
noise. This analysis indicates that male population is higher as compared to female
population who has recognised adverse effects of noise in all categories except “Interface
with communication” although the %age difference is not significant (not more than 10%,
which is in case of mental health disorders). This implies that almost equal proportion of
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male and female population is susceptible to adverse effects of noise for each harmful
effect considered in this study.
In case of mental health disorders, male population is highly susceptible only by 10%.
Both communities, male and female, have almost equally recognised that their work
efficiency reduces because of noise pollution, which is very important finding for the
industries. The industries must adapt good methods to reduce the noise level at the
workplace in view of enhancement of efficiency of workforce and hence productivity.
Modern industries have come up with sound enclosures around the industrial machineries
being operated by human beings to prevent noise effects.
Figure-13 : Harmful effect of noise pollution based on gender
Source: Authors’ Work
The response of higher population in both communities indicates that annoyance,
disturb sleep and hearing impairment are the primary health effects of noise. Thus both
communities have addressed noise as big menace to human’s health and life. Author is
treating noise as another form of “modern plague” causing harmful effects silently on
human’s health and life.
6.5.2 In terms of different age group
Figure-14 shows the perception of populations from various age groups about the effect
of noise. The survey data shows that the effect of noise is not similar among various age
groups. Each age group is affected differently by noise.
It can be visualized that higher population (73%, 71%, 61% & 74%) of age group A1< 20
has reported “Annoyance”, “Disturb sleep”, “Effect on hearing” and “Interfere with
communication” as adverse effects on human health due to noise.
An almost equal proportion of higher population (51%, 52%, 57%, 60% & 52%) of age
group A220-40 has also reported “Annoyance”, “Disturb sleep”, “Effect on hearing”,
“Reduce Working Efficiency” and “Interfere with communication” as harmful effects of
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noise. A mixed proportion of population (63%, 56%, 57%, 74%, 55% & 46%) of age
group A340-60 years has reported “Annoyance”, “Disturb sleep”, “Effect on hearing”,
“Reduce Working Efficiency” and “Interfere with communication” and “Mental health
disorders as bad effects on human health and life due to noise.
A proportion of higher population (88% & 90%) of age group A4>60 years has reported
“Annoyance” and “Disturb sleep” as negative effects on human health due to noise.
Figure-14 : Harmful effect of noise pollution based on different age group
Source: Authors’ Work
It is surprising to note that even youngsters (with a significant population of 61%) have
started coming up with hearing adverse impact caused by noise hazard. This implies that
youngsters are also victim of noise at large scale. High working efficiency of employees is
always a desirable parameter by all industries. The employees working age normally is 20-
60 years in the world. The analysis shows shocking results on reduction of Working
Efficiency. A proportion of 60% in age group A220-40 and 74% in age group A340-60 have
reported reduction in working efficiency due to noise. Similarly significant population of
the same age group (51% & 63% of A220-40 and 52% & 56% of A340-60) have acknowledged
annoyance and disturbed sleep which further will reduce the efficiency of the human
beings. In nutshell, noise has emerged as the biggest cause of disability at workplace and is
becoming big threat & challenge to industries.
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6.6 Suggestions to control Noise Pollution
6.6.1 In terms of Male and Female
Figure-15 shows %age of male and female respondents for probable solutions towards
noise pollution. The analysis shows that there is no major difference (observed less than
15%) in proportions of male and female populations with regard to proposed set of
probable solutions towards noise pollution. In general, a set of a significant proportion of
respondents in all age groups feel that education awareness programmes, technological
solutions and government efforts can help control the noise level. A small proportion of
respondents believe that police and civil administration could also facilitate checking of
noise levels, if empowered. A small %age of respondents also suggests engaging NGOs
(Non-government organization) for invoking various activities towards reduction of noise
level. Thus, Male and female groups do not seem to differ regarding alternative methods of
controlling the noise-level. Predominantly, male as well as female respondents advocate
public education. The analysis also suggests a multi-dimensional approach to achieve goal
of noise level reduction i.e. a single measure cannot achieve the goal of noise-reduction.
Figure-15 : Responses on suggestions to control noise by male and female
Source: Authors’ Work
6.6.2 In terms of different age group
Figure-16 indicates %age of respondents towards a proposed set of probable solutions
to achieve noise level reduction. The major response in term of age groups is almost
similar to that what we have seen in case of male and female respondents i.e. a significant
proportion of respondents in all age groups believe that education awareness programmes,
technological solutions and government efforts. Respondents have given less emphasis to
solutions of “Empowering Police”, “Engaging NGO” and “Empowering Civil
Authorities”. Empowering the police is rated as a tool for control of noise by smaller
proportion of people in total sample. Thus, change in public attitude by awareness
programmes of government, various agencies, NGOs and other civil measures (enforcing
strict laws) could help us reduce or prevent the noise pollution. The most important
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measure for noise reduction is technical solutions. They attack directly the source of the
noise. All other measures attack the consequences without removing the noise source.
Figure-16 : Responses on suggestions to control noise by different age groups
Source: Authors’ Work
6.7 Self-Initiative to control Noise Pollution
The respondents were asked to respond to question - Being a responsible citizen of
India, have you taken any self-initiative contributing towards reduction of Noise Pollution
(Yes / No).
Figure-17 & Figure-18 show the results of analysis of this survey on the basis of
gender and age groups respectively. This analysis indicates that male population (64%)
seems more responsible towards reduction of noise as compared to female population
(55%), however the difference is not significant (only 9%).
In terms of age-group, we found that population of age-group 40-60 years (mature
group of population) are highly responsible (78%) towards noise reduction. However only
36% of population of age-group > 60 years have shown their ability to take self-initiatives
for noise reduction. Only 68% of population of age-group 20-40 was found interested to
reduce noise level. A surprising result of this study is that only 48% of youngsters (up to
20 years) responded to participate in noise reduction self-initiatives. Thus, above results
suggests a need motivating population of all age groups to take self-initiatives towards
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noise reduction. It is a collective responsibility and every community member should
contribute on different levels.
Figure-17 : Self-Initiative to control
Noise Pollution based on Gender
Figure-18 : Self-Initiative to control Noise
Pollution based on Age Group
Source: Authors’ Work Source: Authors’ Work
7. Conclusion
This study revealed that male community is more aware about the noise pollution
compared to female community. However most of the community, especially in the
metropolitan cities, is ignorant of what constitutes noise pollution as well as its adverse
socio-economic & health impacts. The control of noise pollution has been hampered by
insufficient knowledge of its harmful effects on human beings. Hence it is established that
to curb the noise pollution, people should realise the harmful effects of noise pollution.
In India, noise exposure is increasing. In this study, it is established that traffic and
loudspeakers sound as noise are major sources of outdoor noise pollutants. Primarily
“traffic volume” expanded by road, rail and air traffic as a noise has gained wider
recognition in terms of increasingly serious risk to human health. In case of indoor
pollutants, television and different home appliances are turned out to be major noise
sources. The examination showed that proportion of female’s population as compared to
proportion of males’ population is almost same with respect to each sources of noise and
hence %age variation between male and female population is not significant. In this study,
it is important to note that even youngsters are also victim of noise at large scale.
This study also investigated that noise affects human in several ways and male &
female population is equally susceptible to adverse effects of noise. Noise extensively
results in annoyance, disturb sleep, harmful effect on hearing, reduce working efficiency
and interfere with communication however sleep disturbance and annoyance, mostly
related to road traffic noise, comprise the main burden of environmental noise.
Public awareness programmes, education and technological solutions appeared to be
the best methods to achieve the goal of noise reduction as suggested by the respondents.
However, government and NGOs can also play a significant role in putting efforts towards
reduction of noise level by establishing & enforcing noise guidelines, standards and strict
regulatory framework in the society. A substantial proportion of respondents among
various age-groups suggested empowering police and local administration to control and
monitor the effort of noise reduction.
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8. Practical and Policy Implications
Noise is a complex phenomenon because its adverse effects can be cumulative with
prolonged, continuous, or repeated exposure. Consequently, it is practically inevitable to
monitor, predict, and analyze noise and evaluate its exposure-effects. The findings in this
study have several policy implications.
• Government should develop management strategies and action plans for noise control.
The empirical evidence gathered through this study can be employed for developing
appropriate legal and public action programme.
• Awareness programs to disseminate knowledge about harmful effects of noise on
human health and routine life.
• To regulate the industrial noise originating from machinery using sound enclosure and
other technological advancements
9. Recommendations
Noise pollution is very harmful to human health. Preventive and control measures have
been recommended in this section
• Education and creating awareness about noise pollution can be the starting point to deal
with the underlying problems. Basic and essential information should be extensively
disseminated, such as noise levels created by common sources of noise pollution,
adverse health effects on both the person creating noise, and the public preventive
measures and conditions punishable under law. Graphic displays in public places are a
good medium to spread the message. School campaigns, health education programs,
and publicizing through print and electronic media can actively address this issue.
• Ban on pressure horns, phasing out of three wheeler autos, maximization of use of
electric vehicles and phasing out diesel and petrol vehicles. High elastic roads
producing low noise during vehicles at high speed.
• Proper planning of roadways, considering their proximity to human settlements and use
of green muffler (extensive plantation of trees on the roadsides) at wider scale.
• Noise attenuation by placing vegetations around buildings has also been recommended.
Keep noisy machines way from bedroom and living areas.
• In industry setting, use of personal protective equipment (PPEs) such as ear muffs and
ear plugs must be made mandatory. In case of machinery, assessing the root cause and
the developing technological solution will deal with reducing noise level.
• Enactment of Policy, Rules and regulations can be another method to deal with it.
• Efficient engineering products, Encouraging use of noise-absorbent materials.
Adequate noise barriers (technologically developed) around silence zones. Fitting
silencers in car, motorcycles and truck to make their engines quieter.
• Good practices to prevent noise-induced ailments in children should be adopted.
• Monitoring of loudspeaker and generator sets to ensure compliance with prescribed
rules. At a time when we are embarking on heavy urbanization and industrialization,
we should not ignore regulating unwanted noise. It is good to see doctors take up the
important role of environmentalists. The ENT (ear-nose-throat) specialists, doctors and
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academicians must be part of the expert panel on noise pollution and must play the role
of environmentalists for better regulations and control of noise.
Above all, awareness of the public and stakeholders is the key component in the
prevention and control of community noise pollution. Involvement of non-governmental
organizations in generating public interest and co-operation, and providing audiological
facilities will immensely help the cause.
***
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Science and Society 011111111111111111111

Investigation & Examination of Noise Pollution - Definition, Sources, Effects, Monitoring and Control

  • 2. ISSN: 2249-2496 Impact Factor: 7.081 183 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com 1. Introduction The word ‘Noise’ is originated from the Latin word “nausea” implying – ‘Unpleasant Sound’, Unwanted Sound’, ‘Sound that is loud’, ‘A Harsh Sound, and ‘Sound that is unexpected’. A sound becomes noise when it is unpleasant, unwanted, loud and unexpected and detrimental physiological and psychological effect on human. A sound can be unpleasant due to intensity of sound, time of exposure, continuity of sound and its frequency. In general, noise is any sound that humans do not want to hear. Noise is one of the environmental pollution that affects the quality of life of particularly of population at urban areas worldwide. It has increased in the modern age of industrialization and technological advancement. According to recent publication by the World Health Organization (WHO, 2018) at least 100 million people are affected by road noise in the European Union and at least 1.6 million years of healthy life are lost every year. In such noisy urban areas, people seem to have become accustomed to the higher noise levels. According to European Commission (1996), it is affecting human behaviour, well-being, productivity and health. Urbanization, economic growth and motorized transport are some of the driving forces for environmental noise exposure and adverse health effects. In India, noise is one of the most pervasive pollutant and growing problem because Indian people generally have traditional liking for noise, consequently noise is often regarded with the lowest priority for control and management. Most of our happy and sad moments of life are expressed through noise. It may be in the form of busting of crackers, playing loud music in parties and marriages, recitation of religious scriptures and hooting in events etc. Thus there is a silent compromise by us to take noise as a normal part of our routine life without realizing its adverse effects on our life and health. That is the one of main reason that the movement against noise pollution is weak in India. The health impacts of environmental noise are a growing concern among both the general public and policy- makers in India. Currently, limited research studies exist on the exposure-effect-response of noise and its sources & controls in the Indian scenario. In view of this, the present research has been carried out in metro city Delhi of India to synthesize noise definition, empirically investigating public reactions towards sources of noise, noise-induced-effect- response of public and control of noise. 2. Purpose Aiming at studying the noise pollution for its definition, sources, effects and control; this study has following research objectives:- a. Understanding and definition of noise in respect of environmental pollution. b. Exploring the indoor and outdoor sources of noise pollution c. To investigate the awareness level of public. d. To investigate the public reactions on sources of noise. e. To examine the public reactions on noise induced health impacts. f. To explore the solutions to control the noise. 3. Understanding and Definition of Noise Synthesis of noise is carried out to arrive at a most appropriate definition of noise. Noise is a “sound without value” or “any noise that is unwanted by the recipient”. The loudness of noise varies from person to person so no precision definition is possible. Sound/noise is measured in dB (Decibel). The difference between sound and noise are often subjective and is a matter of personal opinion, however author has attempted to
  • 3. ISSN: 2249-2496 Impact Factor: 7.081 184 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com explain this difference with the help of Figure-1. Sound (or noise) is the result of pressure variations, or oscillations, in an elastic medium (e.g., air, water, solids), generated by a vibrating surface, or turbulent fluid flow. Sound propagates in the form of longitudinal (as opposed to transverse) waves, involving a succession of compressions and rarefactions in the elastic medium. Sound becomes noise when the three elements (as shown in Figure-1) (i) Sound Pattern, (ii) Sound Intensity and (iii) exposure duration are having values other than specified norms. The general perception of sound in term of intensity of loudness (dB) is provided in Figure-2 and general noise exposure limits are shown in Figure-3. What is pleasant to some ears may be extremely unpleasant to others depending up on number of psychological factors. Figure -1 : Understanding Noise Source:- Authors’ creation Singh, K.P and Singha, S. (1983) defined noise as a type of atmospheric pollution in the form of waves. It is a shadowy public enemy. According to encyclopedia Britainica (1968), noise is defined as any undesired sound in acoustics. Usually, noise is a mixture of many tones combined in a non-musical manner. According to encyclopedia Americana (1968), noise is defined as unwanted sound. The sweetest music, if it disturbs a person who is trying to concentrate or to sleep, is a noise to him, just as the sound of a pneumatic riveting hammer is noise to nearly everyone. In other words, any sound may be noise if circumstances cause it to be disturbing. In its guidelines for community noise (1999), the WHO defined environmental noise as “noise emitted from all sources except for noise at the industrial workplace”. European Union (EU) Directive 2002/49/EC on the management of environmental noise (2002) defined environmental noise as “unwanted or harmful outdoor sound created by human activities, including noise from road, rail, airports and from industrial sites”. W. W. Seto (1971) and B.G. Liptak et al. (1997) also argued that noise is simply anything that we hear and is subjectively defined as unpleasant or unwanted sound. Consequently, a sound can be noise to one person and not to others, or noise at one time and not at other times. So we can say that sound loud enough to be harmful is called noise without regard to its other characteristics. According to Environmental Health Criteria-126 'noise is considered as any unwanted sound that may
  • 4. ISSN: 2249-2496 Impact Factor: 7.081 185 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com adversely affect the health and well-being of individuals or the populations'. H. S. Bhatia (1998) defined noise as any sound independent of loudness that can produce an undesired physiological or psychological effect in an individual and that may interfere with the social ends of an individual or group. These social ends include all of our activities like communication, work, and sleep etc. The Wilson committee of Britain (1963) defined noise as sound which is undesired by the recipient. Figure -2 : Perception level of sound Figure -3 : Noise exposure limits Source:- Compilation by Authors Source:- Compilation by Authors Therefore, in this study, we can arrive at following most appropriate definition of noise in respect of ambient air quality:- “Noise, in context of environmental pollution, is an unpleasant & unwanted excessive sound (or combination of sounds) above than specified limits [dB(A)] in a particular area emitted from any source; which is undesired & disagreeable to the recipient due to ‘adverse effects on his health’ like damage to hearing, disrupt sleep, hypertension, high blood pressure, cognitive impairment & other diseases and ‘bad effects on his routine life’ like annoyance, discomfort, interference with speech & communication, reduction in efficiency of work performance & disturbance to his normal activities.” 4. Literature Review 4.1 Sources of Noise Pollution There is a need to first identify sources of noise to deal effectively with problem of noise. In India, the increasing ambient noise levels in public places are resulted from various sources like industrial activity, construction activity, fire crackers, sound producing instruments, generator sets, loud speakers, public address systems, music systems, vehicular horns, other mechanical devices, stone crushing machine, defence equipment, television, refrigerator, air conditioners and other home appliances etc. As shown in Figure-4, all these sources of noise pollution can be broadly categories as indoor and outdoor noise pollutants. The indoor noise pollutants are associated with human activities within the building, operation of building services and office equipment. These may include door slam, footfall (especially in multi-story buildings), conversation, radio and television sets, fans and air-conditioners, home appliances and motorized appliances such as power generating sets (Ogunsote, 2010). Outdoor noise pollutants constitute the major sources of environmental noise. The noise caused by outdoor pollutants may be
  • 5. ISSN: 2249-2496 Impact Factor: 7.081 186 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com difficult to control from the source. They include, but are not limited to the following:- noise from traffic and automobiles; noise from industries like quarries and mining industries; noise from pedestrians; noise from religious institutions like churches and mosques; noise from advertising agents and hawkers; noise from rallies like political campaigns, and so on (Ogunsote, 2010). Figure - 4 : Various Indoor and Outdoor Noise Pollutants Source: Authors’ compilation Further population, unawareness about harmful effects of noise pollution, industrialization advancement and advance motorized transport are some of the major contributors for environmental noise. Day & night, a large number of cars, trucks, motorcycles, air-flights and other motorized vehicles criss-cross the cities and resulting noise pollution. Table-1 : Typical sound levels encountered in daily life and industry Activity Sound Level dB(A) Graphical scale of sound level in respects of transport oriented sound levels Desert 10 Rustling Leaves 20 Room in a quiet dwelling at midnight 32 Soft whispers at 5 feet 34 Men’s clothing department of large store 53 Window air conditioner 55 Conversational Speech 60 Household department of large store 62 Busy restaurant 65 Vacuum cleaner in private residence 69 Ringing alarm clock at 2 feet 80 Loudly reproduced orchestral music 82 Prolonged exposure - hearing damage 85 Lorry or motorbike close by 90 Rock concert , loud disco 100 Pneumatic Drill 110 Jet aircraft take-off 130 Gunshots, explosions 140 Source: Tam 2000 Source :World Bank, 1997
  • 6. ISSN: 2249-2496 Impact Factor: 7.081 187 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com According to Birgitta and Lindvall (1995), road traffic, jet planes, garbage trucks, construction equipment, manufacturing processes, and lawn mowers are some of the major sources of this unwanted sounds that are routinely broadcasted into the air. Ritovska et al., (2004) also emphasized that improper use of horn by the traffic and wide use of loudspeakers in Indian religious and social ceremonies are major noise pollutants causing health risk to human. As per Goines and Hagler (2007), noise is a major environmental risk of the global world, originating from a different variety of sources including traffic, which plays main role in noise pollution. It is important to have an understanding of sound levels we typically encountered in our daily routine life. Table-1 provides a list of sound levels from typical situations along with a graphic scale of transport oriented sound levels. 4.2 Effects of Noise Pollution Noise impacts health. The role of noise as an environmental pollutant and its impact on health are being increasingly recognized. The effect of noise on any human being may be psychological or physiological (Ogunsote, 2010; Adedeji and Folorunsho, 2010). Generally, sound is considered as noise pollutant having intensity more than 60 dB. Environmental noise is a psycho-social stressor that affects subjective well-being and physical health (WHO 1999; van Kamp I et. al 2012; EPoN 2010). Noise degrades environment and also causes health hazard to human beings. Exposure to noise for a continuous period of time will have many serious health issues, which may be temporary or permanent. Table-2 provides the details of different sound levels and their harmful effects. Even relatively low levels of noise affect human health adversely (Kiernan, 1997). It may cause hypertension, hearing loss, sleep disruption, cognitive impairment in children, tinnitus, reduced productivity, absenteeism and accidents, cardiovascular disease, annoyance & frustration reactions, social handicaps, negative social behaviour, high blood pressure, anxiety & stress related illness, memory loss, severe depression, and panic attacks. Table-2 : Different sound levels and harmful effects Noise level (dBA) Possible psychological and physiological effects. 65 Annoyance, mental and physical fatigue. 90 Very long exposure may cause permanent hearing loss. 100 Short exposure may cause temporary damage; long exposure may cause permanent damage. 120 Pain. 150 Immediate loss of hearing. Source: : Ogunsote (1991) Epidemiological studies on the relationship between transportation noise (particularly road traffic and aircraft noise) and cardiovascular effects have been carried out on adults and on children. Both road traffic noise and aircraft noise increase the risk of high blood pressure. At the same equivalent noise level, annoyance and self-reported sleep disturbance are usually highest for aircraft noise, and higher for road compared with rail traffic noise (Miedema and Oudcshoorn, 2001). Bond (1996) revealed that the effects of excessive noise could be so severe that either there is a permanent loss of memory or a psychiatric disorder .It disturbs and interferes with activities of the individual, including concentration, communication, relaxation and sleep. Children may be exposed to noise for many of their childhood years and the consequences of long-term noise exposure on reading
  • 7. ISSN: 2249-2496 Impact Factor: 7.081 188 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com comprehension and further cognitive development remain unknown. Many studies have shown negative effects of noise on reading and memory in children (Evans GW, Hygge S, 2007; Evans GW, Lepore SJ, 1993). Tasks affected are those involving central processing and language, such as reading comprehension, memory and attention (Haines MM et al. 2007). A study in London found that 340 children are exposed to the air craft noise of ages 8-11 resulting in annoyance, poor reading and comprehension (Hagler, 1999). In another research, children who were exposure to noise levels above 55 dB they have low attention, less social adaptability, and have opposite behaviour to others compared to children (Costa et al., 2013). Therefore exposure during critical periods of learning at school could potentially impair development and have a lifelong effect on educational attainment. Noise disturbs communication, concentration, relaxation and sleep. Chronic long-term exposure to transportation noise has been shown to be associated with the prevalence and incidence of cardiovascular diseases, including hypertension, ischemic heart diseases and stroke (Babisch W, 2014). Large scale epidemiological studies have been carried out for a long time (Babisch, 2000). Figure-5 shows a proposed reaction scheme for the effects of noise on the organism (Babisch W, 2002). Figure-5 : Noise effects reaction scheme Source: Adopted from Babisch W (2002), Authors’ re-creation Sufficient undisturbed sleep is necessary to maintain performance during the day as well as for general good health (Banks S, Dinges DF, 2007). The human organism recognizes, evaluates and reacts to environmental sounds even while asleep (Oswald I et al., 2007). Environmental noise may badly affect the restorative ability of sleep by means of repeatedly exposure to disrupt sleep due to noise. The repeatedly acute and chronic sleep disturbance due to noise may further affect other things like energy of body to perform various tasks, ability to receive and understand other’s communication, signal detection ability, memory consolidation, creativity, risk taking ability and risk of accidents.
  • 8. ISSN: 2249-2496 Impact Factor: 7.081 189 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com Another noise induced bad effect on health is tinnitus. To put it in terms of auditory abilities, tinnitus is the inability to perceive silence (Leroux T, Lalonde M., 1993). Thus tinnitus is the general term for sound perception (for instance, roaring, hissing or ringing) that cannot be attributed to an external sound source. It is widely believed that mild, occasional or acute temporary tinnitus is experienced by nearly everybody in their lifetime at some time or another (MacFadden D., 1982). The severity of health effects due to noise versus the number of people affected is schematically presented by Figure-6. Figure-6 : Severity of health effects of noise and number of people affected Source: Babisch Based on the systematic review of evidence produced by epidemiological and experimental studies, the relationship between night noise exposure and health effects can be summarized as below (Table -3). Table-3 : Effects of different levels of night noise on the population’s health Average night noise Health effects observed in the population level over a year Lnight,outside Health effects observed in the population (Note. The guidelines assume an average attenuation of 21 dB(A) between inside and outside noise levels.) Up to 30 dB Although individual sensitivities and circumstances may differ, it appears that up to this level no substantial biological effects are observed. Lnight,outside of 30 dB is equivalent to the no observed effect level (NOEL) for night noise. 30 to 40 dB A number of effects on sleep are observed from this range: body movements, awakening, self-reported sleep disturbance, arousals. The intensity of the effect depends on the nature of the source and the number of events. Vulnerable groups (for example children, the chronically ill and the elderly) are more susceptible. However, even in the worst cases the effects seem modest. Lnight,outside of 40 dB is equivalent to the lowest observed adverse effect level (LOAEL) for night noise 40 to 55 dB Adverse health effects are observed among the exposed population. Many people have to adapt their lives to cope with the noise at night. Vulnerable groups are more severely affected. Above 55 dB The situation is considered increasingly dangerous for public health. Adverse health effects occur frequently, a sizeable proportion of the population is highly annoyed and sleep-disturbed. There is evidence that the risk of cardiovascular disease increases. Source: Night noise guidelines for Europe (38).
  • 9. ISSN: 2249-2496 Impact Factor: 7.081 190 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com From above literature review, it is evident that noise pollution results many bad effects on human health and it is therefore of utmost importance to take practical action to limit and control excessive environmental noise. 4.3 Controls of Noise Pollution It is considered necessary to regulate and control the noise producing and generating sources with the objective of maintaining the ambient air quality standards in respect of noise. In India, the Noise Pollution (Regulation and Control) Rules, 2000 have been framed under the Environment (Protection) Act, 1986. These are a set of guidelines with the standard prescribed limits for regulation and control of noise. The ambient levels of noise for different areas / zones specified in the rules are indicated in Table-4. Table-4 : Ambient air quality standards in respect of noise Area Code Category of Area/ Zone Limits in dB* Day Time Night Time (A) Industrial Area 75 70 (B) Commercial Area 65 55 (C) Residential Area 55 45 (D) Silence Zone 50 40 Source: Environment (Protection) Act, 1986 as amended in 2002. Notes regarding Table-4 :- *The limit in dB denotes the time-weighted average of the level of sound in decibels on Scale A which is relatable to human hearing. 1. Day time shall mean from 6.00 a.m. to 10.00 p.m. 2. Night time shall mean from 10.00 p.m. to 6.00 a.m. 3. Silence zone is an area comprising not less than 100 meters around hospitals, educational institutions, courts, religious places or any other area which is declared as such by competent authority. 4. Mixed categories of areas may be declared as one of the four above mentioned categories by competent authority. The Central Pollution Control Board (CPCB) has the responsibility to regulate and control sources of Noise Pollution with the objective of maintaining the ambient air quality standards. From above literature review it is observed that experimental knowledge related to noise is available in literature but less research studies were found based on interaction with real life and practical world like how noise pollution is understood by human/public, how much knowledgeable they are for its harmful effects and what they are doing to reduce and control it. To fill gap, author has tried to attempt this study. 5. Research Methodology 5.1 Location Location is very important factor for this study. Many researches have indicated high levels of sound pollution in different urban areas. Delhi is the capital city of India and is regarded as the heart of the nation. Delhi's urban area is now considered to extend beyond the NCT (National Capital Territory of Delhi) boundaries, and include the neighbouring satellite cities of Ghaziabad, Faridabad, Gurgaon and Noida in an area now called National Capital Region (NCR) and had an estimated population of over 26 million people, making it the world's second-largest urban area according to the United Nations (2016). Apart from country’s largest urban agglomerations, Delhi is an important commercial, transport, and cultural hub. Therefore Delhi is chosen for this study.
  • 10. ISSN: 2249-2496 Impact Factor: 7.081 191 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com 5.2 Sample, Data and Techniques This empirical study is based on primary data collected through a structured online questionnaire. The sample represents a cross-section of different age groups, gender and educational levels. Total 350 responses were collected. The analysis has been carried out with the help of ‘percentages technique’ and ‘cross classifications’ in terms of ‘age’ as well as ‘gender’ on awareness of noise pollution, sources of noise, effects of noise, and suggestions to control noise. 6. Analysis, Results and Findings 6.1 Respondents Demographics The study is based on cross-classification in term of age and gender. The demographics details of respondents are shown in Table-5. Table-5 : Respondents Demographics Characteristics Value %age Total Respondents 350 100% Gender Male 199 57% Female 151 43% Age-Group Up to 20 ( Say A1<20 ) 66 19% 20-40 ( Say A220-40 ) 120 34% 40-60 ( Say A340-60 ) 91 26% Above 60 ( Say A4>60 ) 73 21% Education Doctorate 45 13% Post-Graduation 148 42% Graduation 126 36% Diploma 7 2% Others 24 7% Source: Authors’ Survey Data 6.2 Awareness about Noise Pollution 6.2.1 In terms of Male and Female Awareness is major agent which can contribute to control and hence reduce the noise pollution. The awareness level of respondents based on gender is sown in Figure-6, which presents the %age of male and female respondents answering questions Q1, Q2, Q3 and Q4 as Yes/No. It is evident from Figure-7 that in general, male respondents are more aware about the noise pollution as compared to female (see % age “Yes” response for MaleQ1-80%, MaleQ2- 43%, MaleQ3-77%, MaleQ4-74%) except MaleQ5-65% where female are more aware; FemaleQ5-68%. However %age difference in “Yes” responses of male and female is not significant (e.g. 80-64 = 16%, 43-37 = 6%, 77-70 = 7%, 74-66 = 8%, 68-65 = 3%); which implies that on an average, the awareness of noise pollution is almost equal among male and female community. The “No” response of 23% by male community and 30% by female community against question Q3 implies that almost one third of the community,
  • 11. ISSN: 2249-2496 Impact Factor: 7.081 192 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com especially in the Indian subcontinent, is not aware that noise can cause any health damages although environmental noise has severe negative impact on human health. This calls for implementations of actions and initiatives to spread the awareness among Indian population about harmful effects of noise pollution. The “No” response of 57% of male community and 63% of female community towards question Q2 also calls for dissemination of knowledge of limits of noise level. Thus, there is less awareness in Indian population regarding noise impacts human health negatively and hence there is need to increase the awareness about noise pollution among both male and female for better understanding of noise pollution and hence it’s monitoring & control. Figure-7 : Awareness about noise pollution in terms of male and female respondents Source: Authors’ Work 6.2.2 In terms of different age group The awareness level of respondents based on age groups is sown in Figure-8, which presents the %age of various respondents from age groups A1<20, A220-40, A340-60 & A4>60 answering questions Q1, Q2, Q3 and Q4 as Yes/No. The analysis indicates that very large proportion of population in age group A220-40 (valuing “Yes” as 85%, 55%, 91%, 87% & 74% for all questions Q1,Q2,Q3,Q4 & Q5 respectively) and age group A340-60 (valuing “Yes” as 89%, 54%, 92%, 88% & 71% for all questions Q1,Q2,Q3,Q4 & Q5 respectively) are more aware about noise pollution as compared to population in youngest age group of A1<20 (valuing “Yes” as 53%, 24%, 56%, 53% & 62% for all questions Q1,Q2,Q3,Q4 & Q5 respectively) and oldest age group A4>60 (valuing “Yes” as 47%, 86%, 91%, 87% & 74% for all questions Q1,Q2,Q3,Q4 & Q5 respectively). The awareness about the most important question Q3 (Do you know that noise impacts to the human health?) is poor in
  • 12. ISSN: 2249-2496 Impact Factor: 7.081 193 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com respondents in age group of A1<20 & A4>60 (%age of “Yes” population is A1-56%, A4-41%). The response against question Q2 implies that significant population in all age groups does not know the about norms of noise limits in their areas. The above analysis brings out most important point that noise pollution is increasing day by day due to one of major reason of lack of awareness of noise pollution and its harmful effects. Figure-8 : Awareness of noise pollution based on different age groups Source: Authors’ Work 6.3 Reactions of respondents towards Outdoor Noise Pollutants 6.3.1 In terms of Male and Female The analysis of impact of outdoor sources of noise pollution on male community and female community differently is shown in Figure -9. The Figure-8 presents the % age of
  • 13. ISSN: 2249-2496 Impact Factor: 7.081 194 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com male and female respondents affected by different outdoor sources of noise. There are significant differences in population (more than 10%) affected by noise generated from “Loudspeakers” and “Parties, Events & Functions” where male population (70% and 50% respectively) is more affected over the female population (54% and 38% respectively). In terms of remaining sources of noise, there is no significant difference in % age (less than 10%) of male population and female population. It implies that other sources of noise (Traffic, Industrial Manufacturing Noise, Religious Functions, Commercial Construction Noise and Neighbourhoods) affect equally to male population as well as female population. Ranking wise, male and female population are highly affected by (1) Traffic followed in descending order by (2) Loudspeakers, (3) Industrial Manufacturing (4) Noise, Parties, Events & Functions, (5) Religious Functions, (6) Commercial Construction Noise and (7) Neighbourhoods. Thus, “Traffic Volume” expanded by road, rail and air traffic as a noise has gained wider recognition in terms of increasingly serious risk to human health. Figure-9 : Impact of various outdoor noise pollutants based on gender Source: Authors’ Work 6.3.2 In terms of different age group The Figure-10 presents the % age of respondents of different age groups affected by different outdoor sources of noise. The analysis indicates that a very large proportion of respondents (ranging from 79% to 89%) in each age group are being affected by noise emanating from the “Traffic”. On the other hand, very less proportion of respondents (ranging from 3% to 26%) in all age groups are affected by “Neighbourhoods”. An almost equal proportions of respondents (ranging from 41% to 75%) across different age-groups claim that noise originating from “Loudspeakers” affects them. A relatively small proportion of respondents (ranging from 10% to 55%) acknowledge adverse effect of noise generated by “Commercial Construction”. Majority of respondents with little %age difference across different age groups feel that noise originating from “Religious
  • 14. ISSN: 2249-2496 Impact Factor: 7.081 195 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com Functions”, “Parties, Events & Functions” and “Industrial manufacturing” affects their activities. The highly affected proportion of population due to outdoor noise is from age group A1<20 followed in descending order by age group A340-60, A220-40 and A4>60. The disturbance of the community of youngest age group A1<20 at large is obvious due to education/study period of life. The recognition of harmful effects of outdoor noise by the community of oldest age group A4>60 at small proportion seems true because till age of 60 years people normally get affected to maximum extent and thereafter they feel less impact of noise pollution on their life and health. This analysis brings out that “Traffic” and “Loudspeakers” act as significant sources of outdoor noise pollution. Thus population at large in Delhi is becoming victim of noise pollution mainly originating from “Traffic” and “Loudspeakers”. Figure-10 : Impact of various outdoor noise pollutants based on different age groups Source: Authors’ Work
  • 15. ISSN: 2249-2496 Impact Factor: 7.081 196 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com 6.4 Reactions of respondents towards Indoor Noise Pollutants 6.4.1 In terms of Male and Female Figure-11 presents the %age of male and female respondents affected by different indoor sources of noise. The analysis indicates that there are no significant differences in %age of population (all are less than 10%) affected by noise generated from indoor sources. It implies that all indoor sources of noise affect equally to male population as well as female population. Ranking wise, male and female population are highly affected by (1) TV (Television) followed in descending order by (2) Different home appliances, (3) Power Generators, (4) Air Cooler / Air Conditioners, (5) Family conflict, (6) Refrigerators. An almost equal %age of male and female population has recognised that noise originating from “TV (Television)”, and “Different home appliances” affects their activities. Thus, “TV (Television)”, and “Different home appliances”, as a noise are mostly considered high serious risk to human health. Figure-11 : Impact of various indoor noise pollutants based on gender Source: Authors’ Work 6.4.2 In terms of different age group The Figure-12 presents the %age of respondents of different age groups affected by different indoor sources of noise. The analysis indicates that a very large proportion of respondents in each age group are being affected by noise emanating from the “Different home appliances” ranging from 33% to 60% and from the “TV (Television)” ranging from 29% to 58%. On the other hand, very less proportion of respondents in all age groups is affected by “Refrigerators” ranging from 5% to 15% and by “Family conflict” ranging from 8% to 36%. An almost equal proportions of respondents (ranging from 41% to 75%) across different age-groups claim that noise originating from “Loudspeakers” affects them. Majority of respondents with significant %age difference across different age groups feel
  • 16. ISSN: 2249-2496 Impact Factor: 7.081 197 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com that noise originating from “Power Generators”, and “Air Cooler / Air Conditioners” affects their activities. The major proportion of respondents (58%) in youngest age group A1<20 feel that they are most affected by the noise from “Air Cooler / Air Conditioners” however on other hand large proportion (60%) of oldest age group A4>60 acknowledge harmful effect due to “Different home appliance”. Highest proportion of age groups A220-40 (58%) and A340-60 (54%) responded that their life is badly affected by the noise originating from TV (television). The noise originating from “Refrigerators” is affecting least population in each age group. Figure-12 : Impact of various indoor noise pollutants based on different age group Source: Authors’ Work Therefore “TV (Television)”, and “Different home appliances”, act as significant sources of indoor noise pollution and affect each age group differently. Thus, large population of metropolitan cities is mostly affected by the noise originating from indoor noise pollutants “TV (Television)”, and “Different home appliances”. 6.5 Reaction of Respondents regarding effect of Noise Pollution 6.5.1 In terms of Male and Female Figure-13 shows the perception of male and female populations about the effect of noise. This analysis indicates that male population is higher as compared to female population who has recognised adverse effects of noise in all categories except “Interface with communication” although the %age difference is not significant (not more than 10%, which is in case of mental health disorders). This implies that almost equal proportion of
  • 17. ISSN: 2249-2496 Impact Factor: 7.081 198 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com male and female population is susceptible to adverse effects of noise for each harmful effect considered in this study. In case of mental health disorders, male population is highly susceptible only by 10%. Both communities, male and female, have almost equally recognised that their work efficiency reduces because of noise pollution, which is very important finding for the industries. The industries must adapt good methods to reduce the noise level at the workplace in view of enhancement of efficiency of workforce and hence productivity. Modern industries have come up with sound enclosures around the industrial machineries being operated by human beings to prevent noise effects. Figure-13 : Harmful effect of noise pollution based on gender Source: Authors’ Work The response of higher population in both communities indicates that annoyance, disturb sleep and hearing impairment are the primary health effects of noise. Thus both communities have addressed noise as big menace to human’s health and life. Author is treating noise as another form of “modern plague” causing harmful effects silently on human’s health and life. 6.5.2 In terms of different age group Figure-14 shows the perception of populations from various age groups about the effect of noise. The survey data shows that the effect of noise is not similar among various age groups. Each age group is affected differently by noise. It can be visualized that higher population (73%, 71%, 61% & 74%) of age group A1< 20 has reported “Annoyance”, “Disturb sleep”, “Effect on hearing” and “Interfere with communication” as adverse effects on human health due to noise. An almost equal proportion of higher population (51%, 52%, 57%, 60% & 52%) of age group A220-40 has also reported “Annoyance”, “Disturb sleep”, “Effect on hearing”, “Reduce Working Efficiency” and “Interfere with communication” as harmful effects of
  • 18. ISSN: 2249-2496 Impact Factor: 7.081 199 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com noise. A mixed proportion of population (63%, 56%, 57%, 74%, 55% & 46%) of age group A340-60 years has reported “Annoyance”, “Disturb sleep”, “Effect on hearing”, “Reduce Working Efficiency” and “Interfere with communication” and “Mental health disorders as bad effects on human health and life due to noise. A proportion of higher population (88% & 90%) of age group A4>60 years has reported “Annoyance” and “Disturb sleep” as negative effects on human health due to noise. Figure-14 : Harmful effect of noise pollution based on different age group Source: Authors’ Work It is surprising to note that even youngsters (with a significant population of 61%) have started coming up with hearing adverse impact caused by noise hazard. This implies that youngsters are also victim of noise at large scale. High working efficiency of employees is always a desirable parameter by all industries. The employees working age normally is 20- 60 years in the world. The analysis shows shocking results on reduction of Working Efficiency. A proportion of 60% in age group A220-40 and 74% in age group A340-60 have reported reduction in working efficiency due to noise. Similarly significant population of the same age group (51% & 63% of A220-40 and 52% & 56% of A340-60) have acknowledged annoyance and disturbed sleep which further will reduce the efficiency of the human beings. In nutshell, noise has emerged as the biggest cause of disability at workplace and is becoming big threat & challenge to industries.
  • 19. ISSN: 2249-2496 Impact Factor: 7.081 200 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com 6.6 Suggestions to control Noise Pollution 6.6.1 In terms of Male and Female Figure-15 shows %age of male and female respondents for probable solutions towards noise pollution. The analysis shows that there is no major difference (observed less than 15%) in proportions of male and female populations with regard to proposed set of probable solutions towards noise pollution. In general, a set of a significant proportion of respondents in all age groups feel that education awareness programmes, technological solutions and government efforts can help control the noise level. A small proportion of respondents believe that police and civil administration could also facilitate checking of noise levels, if empowered. A small %age of respondents also suggests engaging NGOs (Non-government organization) for invoking various activities towards reduction of noise level. Thus, Male and female groups do not seem to differ regarding alternative methods of controlling the noise-level. Predominantly, male as well as female respondents advocate public education. The analysis also suggests a multi-dimensional approach to achieve goal of noise level reduction i.e. a single measure cannot achieve the goal of noise-reduction. Figure-15 : Responses on suggestions to control noise by male and female Source: Authors’ Work 6.6.2 In terms of different age group Figure-16 indicates %age of respondents towards a proposed set of probable solutions to achieve noise level reduction. The major response in term of age groups is almost similar to that what we have seen in case of male and female respondents i.e. a significant proportion of respondents in all age groups believe that education awareness programmes, technological solutions and government efforts. Respondents have given less emphasis to solutions of “Empowering Police”, “Engaging NGO” and “Empowering Civil Authorities”. Empowering the police is rated as a tool for control of noise by smaller proportion of people in total sample. Thus, change in public attitude by awareness programmes of government, various agencies, NGOs and other civil measures (enforcing strict laws) could help us reduce or prevent the noise pollution. The most important
  • 20. ISSN: 2249-2496 Impact Factor: 7.081 201 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com measure for noise reduction is technical solutions. They attack directly the source of the noise. All other measures attack the consequences without removing the noise source. Figure-16 : Responses on suggestions to control noise by different age groups Source: Authors’ Work 6.7 Self-Initiative to control Noise Pollution The respondents were asked to respond to question - Being a responsible citizen of India, have you taken any self-initiative contributing towards reduction of Noise Pollution (Yes / No). Figure-17 & Figure-18 show the results of analysis of this survey on the basis of gender and age groups respectively. This analysis indicates that male population (64%) seems more responsible towards reduction of noise as compared to female population (55%), however the difference is not significant (only 9%). In terms of age-group, we found that population of age-group 40-60 years (mature group of population) are highly responsible (78%) towards noise reduction. However only 36% of population of age-group > 60 years have shown their ability to take self-initiatives for noise reduction. Only 68% of population of age-group 20-40 was found interested to reduce noise level. A surprising result of this study is that only 48% of youngsters (up to 20 years) responded to participate in noise reduction self-initiatives. Thus, above results suggests a need motivating population of all age groups to take self-initiatives towards
  • 21. ISSN: 2249-2496 Impact Factor: 7.081 202 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com noise reduction. It is a collective responsibility and every community member should contribute on different levels. Figure-17 : Self-Initiative to control Noise Pollution based on Gender Figure-18 : Self-Initiative to control Noise Pollution based on Age Group Source: Authors’ Work Source: Authors’ Work 7. Conclusion This study revealed that male community is more aware about the noise pollution compared to female community. However most of the community, especially in the metropolitan cities, is ignorant of what constitutes noise pollution as well as its adverse socio-economic & health impacts. The control of noise pollution has been hampered by insufficient knowledge of its harmful effects on human beings. Hence it is established that to curb the noise pollution, people should realise the harmful effects of noise pollution. In India, noise exposure is increasing. In this study, it is established that traffic and loudspeakers sound as noise are major sources of outdoor noise pollutants. Primarily “traffic volume” expanded by road, rail and air traffic as a noise has gained wider recognition in terms of increasingly serious risk to human health. In case of indoor pollutants, television and different home appliances are turned out to be major noise sources. The examination showed that proportion of female’s population as compared to proportion of males’ population is almost same with respect to each sources of noise and hence %age variation between male and female population is not significant. In this study, it is important to note that even youngsters are also victim of noise at large scale. This study also investigated that noise affects human in several ways and male & female population is equally susceptible to adverse effects of noise. Noise extensively results in annoyance, disturb sleep, harmful effect on hearing, reduce working efficiency and interfere with communication however sleep disturbance and annoyance, mostly related to road traffic noise, comprise the main burden of environmental noise. Public awareness programmes, education and technological solutions appeared to be the best methods to achieve the goal of noise reduction as suggested by the respondents. However, government and NGOs can also play a significant role in putting efforts towards reduction of noise level by establishing & enforcing noise guidelines, standards and strict regulatory framework in the society. A substantial proportion of respondents among various age-groups suggested empowering police and local administration to control and monitor the effort of noise reduction.
  • 22. ISSN: 2249-2496 Impact Factor: 7.081 203 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com 8. Practical and Policy Implications Noise is a complex phenomenon because its adverse effects can be cumulative with prolonged, continuous, or repeated exposure. Consequently, it is practically inevitable to monitor, predict, and analyze noise and evaluate its exposure-effects. The findings in this study have several policy implications. • Government should develop management strategies and action plans for noise control. The empirical evidence gathered through this study can be employed for developing appropriate legal and public action programme. • Awareness programs to disseminate knowledge about harmful effects of noise on human health and routine life. • To regulate the industrial noise originating from machinery using sound enclosure and other technological advancements 9. Recommendations Noise pollution is very harmful to human health. Preventive and control measures have been recommended in this section • Education and creating awareness about noise pollution can be the starting point to deal with the underlying problems. Basic and essential information should be extensively disseminated, such as noise levels created by common sources of noise pollution, adverse health effects on both the person creating noise, and the public preventive measures and conditions punishable under law. Graphic displays in public places are a good medium to spread the message. School campaigns, health education programs, and publicizing through print and electronic media can actively address this issue. • Ban on pressure horns, phasing out of three wheeler autos, maximization of use of electric vehicles and phasing out diesel and petrol vehicles. High elastic roads producing low noise during vehicles at high speed. • Proper planning of roadways, considering their proximity to human settlements and use of green muffler (extensive plantation of trees on the roadsides) at wider scale. • Noise attenuation by placing vegetations around buildings has also been recommended. Keep noisy machines way from bedroom and living areas. • In industry setting, use of personal protective equipment (PPEs) such as ear muffs and ear plugs must be made mandatory. In case of machinery, assessing the root cause and the developing technological solution will deal with reducing noise level. • Enactment of Policy, Rules and regulations can be another method to deal with it. • Efficient engineering products, Encouraging use of noise-absorbent materials. Adequate noise barriers (technologically developed) around silence zones. Fitting silencers in car, motorcycles and truck to make their engines quieter. • Good practices to prevent noise-induced ailments in children should be adopted. • Monitoring of loudspeaker and generator sets to ensure compliance with prescribed rules. At a time when we are embarking on heavy urbanization and industrialization, we should not ignore regulating unwanted noise. It is good to see doctors take up the important role of environmentalists. The ENT (ear-nose-throat) specialists, doctors and
  • 23. ISSN: 2249-2496 Impact Factor: 7.081 204 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com academicians must be part of the expert panel on noise pollution and must play the role of environmentalists for better regulations and control of noise. Above all, awareness of the public and stakeholders is the key component in the prevention and control of community noise pollution. Involvement of non-governmental organizations in generating public interest and co-operation, and providing audiological facilities will immensely help the cause. *** Bibliography Barrigón Morillas, J., Gómez Escobar, V., Méndez Sierra, J., Vílchez Gómez, R., & Trujillo Carmona, J. (2002a). An environmental noise study in the city of Cáceres, Spain. Applied Acoustics, 63(10), 1061-1070. Birgitta, Berglund and Lindvall, Homas (1995). A Draft Document of Community Noise. Who Environmental Health Criteria12, World Health Organization, Geneva. Banks S, Dinges DF (2007). Behavioral and physiological consequences of sleep restriction. Journal of Clinical Sleep Medicine,3, 519–528. Babisch W. (2014). Updated exposure-response relationship between road traffic noise and coronary heart diseases: A meta-analysis. Noise Health,16, 1-9 Babisch W (2006). Transportation noise and cardiovascular risk: updated review and synthesis of epidemiological studies indicate that the evidence has increased. Noise & Health, 8,1–29. Babisch W (2000). Traffic noise and cardiovascular disease: epidemiological review and synthesis. Noise & Health, 2(8), 9–32. Bond, Michael (1996). Plagued by noise. New Scientist, 11(16), 14-15. Chang, T. Y., Lin, H. C., Yang, W. T., Bao, B. Y., & Chan, C. C. (2012). A modified Nordic prediction model of road traffic noise in a Taiwanese city with significant motorcycle traffic. Science of total environment, 15(432), 375-381. Costa, G. D. L., Lacerda, A. B. M. D., & Marques, J. (2013). Noise on the hospital context: impact on nursing professionals’ health. Revista CEFAC, 15(3), 642 652. Di, G., Liu, X., Lin, Q., Zhen, Y., & He, L. (2012). The relationship between urban conbined traffic noise and annoyance. An investigation in Dilian, north of China. Science of total environment, 432, 189-194. D. H. F. Liu, B. G. Liptak, and P. A. Bouis (1997). Environmental Engineers' Handbook, New York: Lewis Publishers. Directive 2002/49/EC of the European Parliament and of the Council of 25 June 2002 relating to the assessment and management of environmental noise. Official Journal of the European Communities, L 189, 12–25. European Commission 1996. Green Paper on Future Noise Policy COM(96), 540. Encyclopaedia Britainica, Vol. 16, 1968. Encyclopaedia Americanna, 2nd ed., 1969. Evans GW, Hygge S. (2007). Noise and cognitive performance in children and adults. In:
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  • 26. ISSN: 2249-2496 Impact Factor: 7.081 207 International Journal of Research in Social Sciences http://www.ijmra.us, Email: editorijmie@gmail.com WHO (199). Guidelines for community noise. Geneva: World Health Organization. World Health Organization (2018). Environmental Noise Guidelines for the European Region; p. 160.