SlideShare a Scribd company logo
A Section 
Overview 
Chapter 1 Environment for Development
“The ‘environment’ is where we live; and 
development is what we all do in attempting 
to improve our lot within that abode. 
The two are inseparable.” 
Our Common Future
Chapter1 
Environment for Development 
Coordinating lead authors: Diego Martino and Zinta Zommers 
Lead authors: Kerry Bowman, Don Brown, Flavio Comim, Peter Kouwenhoven, Ton Manders, Patrick Milimo, 
Jennifer Mohamed-Katerere, and Thierry De Oliveira 
Contributing authors: Dan Claasen, Simon Dalby, Irene Dankelman, Shawn Donaldson, Nancy Doubleday, 
Robert Fincham, Wame Hambira, Sylvia I. Karlsson, David MacDonald, Lars Mortensen, Renata Rubian, 
Guido Schmidt-Traub, Mahendra Shah, Ben Sonneveld, Indra de Soysa, Rami Zurayk, M.A. Keyzer, and 
W.C.M. Van Veen 
Chapter review editor: Tony Prato 
Chapter coordinators: Thierry De Oliveira, Tessa Goverse, and Ashbindu Singh 
Credit: fotototo/Still Pictures
Main messages 
It is 20 years since the report of the World 
Commission on Environment and Development 
(WCED), Our Common Future, emphasized 
the need for a sustainable way of life which 
not only addresses current environmental 
challenges but also ensures a secure society 
well into the future. This chapter analyses 
the evolution of such ideas as well as global 
trends in relation to environment and socio-economic 
development. The following are its 
main messages: 
The world has changed radically since 
1987 – socially, economically and 
environmentally. Global population has 
grown by more than 1.7 billion, from 
about 5 billion people. The global economy 
has expanded and is now characterized 
by increasing globalization. Worldwide, 
GDP per capita (purchasing power parity) 
has increased from US$5 927 in 1987 to 
US$8 162 in 2004. However, growth has 
been distributed unequally between regions. 
Global trade has increased during the past 
20 years, fuelled by globalization, better 
communication, and low transportation 
costs. Technology has also changed. 
Communications have been revolutionized 
with the growth of telecommunications and 
the Internet. Worldwide, mobile phone 
subscribers increased from 2 people per 
1 000 in 1990 to 220 per 1 000 in 2003. 
Internet use increased from 1 person per 
1 000 in 1990 to 114 per 1 000 in 2003. 
Finally, political changes have also been 
extensive. Human population and economic 
growth has increased demand on resources. 
The World Commission on Environment and 
Development (WCED) recognized 20 years 
ago that the environment, economic and social 
issues are interlinked. It recommended that the 
three be integrated into development decision 
making. In defining sustainable development, 
the Commission acknowledged the need 
for both intra- and intergenerational equity 
– development that meets not only today’s 
human needs but also those of more people in 
the future. 
Changing drivers, such as population growth, 
economic activities and consumption patterns, 
have placed increasing pressure on the 
environment. Serious and persistent barriers 
to sustainable development remain. In the past 
20 years, there has been limited integration of 
environment into development decision making. 
Environmental degradation is therefore 
undermining development and threatens 
future development progress. Development is 
a process that enables people to better their 
well-being. Long-term development can only 
be achieved through sustainable management 
of various assets: financial, material, human, 
social and natural. Natural assets, including 
water, soils, plants and animals, underpin 
people’s livelihoods. 
Environmental degradation also 
threatens all aspects of human well-being. 
Environmental degradation has 
been demonstrably linked to human health 
problems, including some types of cancers, 
vector-borne diseases, emerging animal to 
human disease transfer, nutritional deficits 
and respiratory illnesses. The environment 
provides essential material assets and an 
economic base for human endeavour. Almost 
half the jobs worldwide depend on fisheries, 
forests or agriculture. Non-sustainable use 
of natural resources, including land, water, 
forests and fisheries, can threaten individual 
livelihoods as well as local, national and 
international economies. The environment 
can play a significant role in contributing to 
development and human well-being, but can 
also increase human vulnerability, causing 
human migration and insecurity, such as in 
the case of storms, droughts or environmental
mismanagement. Environmental scarcity can 
foster cooperation, but also contribute to 
tensions or conflicts. 
Environmental sustainability, Millennium 
Development Goal 7, is critical to the 
attainment of the other MDG goals. Natural 
resources are the basis of subsistence in many 
poor communities. In fact, natural capital 
accounts for 26 per cent of the wealth of 
low-income countries. Up to 20 per cent of 
the total burden of disease in developing 
countries is associated with environmental 
risks. Poor women are particularly vulnerable 
to respiratory infections related to exposure 
to indoor air pollution. Acute respiratory 
infections are the leading cause of death in 
children, with pneumonia killing more children 
under the age of five than any other illness. 
A combination of unsafe water and poor 
sanitation is the world’s second biggest killer 
of children. About 1.8 million children die 
annually and about 443 million school days 
are missed due to diarrhoea. Clean water 
and air are powerful preventative medicines. 
Sustainable management of natural resources 
contributes to poverty alleviation, helps 
reduce diseases and child mortality, improves 
maternal health, and can contribute to gender 
equity and universal education. 
Some progress towards sustainable 
development has been made since 1987 when 
the WCED report, Our Common Future, was 
launched. The number of meetings and summits 
related to the environment and development 
has increased (for example, the 1992 Rio 
Earth Summit and the 2002 World Summit on 
Sustainable Development), and there has been 
a rapid growth in multilateral environmental 
agreements (for example, the Kyoto Protocol 
and the Stockholm Convention on Persistent 
Organic Pollutants). Sustainable development 
strategies have been implemented at local, 
national, regional and international levels. An 
increasing number of scientific assessments 
(for example, the Intergovernmental Panel on 
Climate Change) have contributed to a greater 
understanding of environmental challenges. In 
addition, proven and workable solutions have 
been identified for environmental problems that 
are limited in scale, highly visible and acute, 
(for example, industrial air and water pollution, 
local soil erosion and vehicle exhaust emission). 
However, some international negotiations 
have stalled over questions of equity and 
responsibility sharing. Interlinkages between 
drivers and pressures on the global environment 
make solutions complex. As a result, action 
has been limited on some issues, for example, 
climate change, persistent organic pollutants, 
fisheries management, invasive alien species 
and species extinction. 
Effective policy responses are needed at all 
levels of governance. While proven solutions 
continue to be used, action should also be 
taken to address both the drivers of change and 
environmental problems themselves. A variety of 
tools that have emerged over the past 20 years 
may be strategic. Economic instruments, such 
as property rights, market creation, bonds and 
deposits, can help correct market failures and 
internalize costs of protecting the environment. 
Valuation techniques can be used to understand 
the value of ecosystem services. Scenarios can 
provide insights on the future impacts of policy 
decisions. Capacity building and education are 
critical to generate knowledge and inform the 
decision making process. 
Society has the capacity to make a difference 
in the way the environment is used to 
underpin development and human well-being. 
The following chapters highlight many of the 
challenges society faces today and provides 
signposts towards sustainable development.
INTRODUCTION 
Imagine a world in which environmental change 
threatens people’s health, physical security, material 
needs and social cohesion. This is a world beset 
by increasingly intense and frequent storms, and 
by rising sea levels. Some people experience 
extensive flooding, while others endure intense 
droughts. Species extinction occurs at rates never 
before witnessed. Safe water is increasingly limited, 
hindering economic activity. Land degradation 
endangers the lives of millions of people. 
This is the world today. Yet, as the World 
Commission on Environment and Development 
(Brundtland Commission) concluded 20 years ago 
“humanity has the ability to make development 
sustainable.” The fourth Global Environment 
Outlook highlights imperative steps needed to 
achieve this vision. 
The fourth GEO assesses the current state of the 
world’s atmosphere, land, water and biodiversity, 
providing a description of the state of environment, 
and demonstrating that the environment is essential 
for improving and sustaining human well-being. 
It also shows that environmental degradation 
is diminishing the potential for sustainable 
development. Policies for action are highlighted to 
facilitate alternative development paths. 
This chapter examines developments since the 
landmark 1987 Brundtland Commission report 
– Our Common Future – placed sustainable 
development much higher on the international policy 
agenda. It examines institutional developments 
and changes in thought since the mid-1980s, and 
explores the relationships involving environment, 
development and human well-being, reviews 
major environmental, social and economic trends, 
and their impacts on environment and human 
well-being, and provides options to help achieve 
sustainable development. 
Subsequent chapters will analyse of environmental 
changes in the atmosphere, land, water and 
biodiversity, both at global and regional levels, 
and will highlight human vulnerability and strategic 
policy interlinkages for effective responses. Positive 
developments since 1987 are described. These 
include progress towards meeting the goals of the 
Montreal Protocol, and the reduction in emissions of 
6 SECTION A: OVERVIEW 
chemicals that deplete the stratospheric ozone layer. 
Yet, the chapters also highlight current environmental 
trends that threaten human well-being: 
® In some cases, climate change is having severe 
effects on human health, food production, security 
and resource availability. 
® Extreme weather conditions are having an 
increasingly large impact on vulnerable human 
communities, particularly the world’s poor. 
® Both indoor and outdoor pollution is still causing 
many premature deaths. 
® Land degradation is decreasing agricultural 
productivity, resulting in lower incomes and 
reduced food security. 
® Decreasing supplies of safe water are 
jeopardizing human health and economic activity. 
® Drastic reductions of fish stocks are creating both 
economic losses and a loss of food supply. 
® Accelerating species extinction rates are threatening 
the loss of unique genetic pools, possible sources 
for future medical and agricultural advances. 
Choices made today will determine how these 
threats will unfold in the future. Reversing such 
adverse environmental trends will be an immense 
challenge. Ecosystem services collapse is a distinct 
possibility if action is not taken. Finding solutions to 
these problems today is therefore urgent. 
This chapter provides a message for action today: 
The Earth is our only home. Its well-being, and 
our own, is imperilled. To ensure long-term well-being, 
we must take an alternative approach 
to development, one that acknowledges the 
importance of environment. 
OUR COMMON FUTURE: EVOLUTION OF 
IDEAS AND ACTIONS 
Two decades ago the Brundtland Commission report 
– Our Common Future – addressed the links between 
development and environment, and challenged 
policy-makers to consider the interrelationships 
among environment, economic and social issues 
when it comes to solving global problems. The report 
examined emerging global challenges in: 
® population and human resources; 
® food security; 
® species and ecosystems; 
® energy; 
® industry; and 
® urbanization.
Gro Harlem Brundtland 
introduces to the General 
Assembly, the report of the World 
Commission on Environment 
and Development in 1987, 
which she chaired. The work 
of the Brundtland Commission 
challenged policy-makers to 
consider the interrelationships 
among environment, economic 
and social issues in efforts to 
solve global problems. 
Credit: UN Photo/Milton Grant 
ENV I RONMENT FOR DE V E LOPMENT 7 
The commission recommended institutional and 
legal changes in six broad areas to address these 
challenges: 
® getting at the sources; 
® dealing with the effects; 
® assessing global risks; 
® making informed choices; 
® providing the legal means; and 
® investing in our future. 
Recommendations emphasized the expansion of 
international institutions for cooperation, and the 
creation of legal mechanisms for environmental 
protection and sustainable development, and also 
stressed the links between poverty and environmental 
degradation. They also called for increased capacity 
to assess and report on risks of irreversible damage to 
natural systems, as well as threats to human survival, 
security and well-being. 
The work of the commission was built on the 
foundation of, among others, the 1972 UN 
Conference on the Human Environment in Stockholm 
and the 1980 World Conservation Strategy, 
which emphasized conservation as including 
both protection and the rational use of natural 
resources (IUCN and others 1991). The Brundtland 
Commission is widely attributed with popularizing 
sustainable development internationally (Langhelle 
1999). It defined sustainable development as 
“development that meets the needs of the present 
generation without compromising the ability of 
future generations to meet their own needs.” The 
commission further explained that, “the concept 
of sustainable development implies limits – not 
absolute limits but limitations imposed by the present 
state of technology and social organization on 
environmental resources and by the ability of the 
biosphere to absorb the effects of human activities.” 
It was argued that, “technology and social 
organization can be both managed and improved 
to make way for a new era of economic growth” 
(WCED 1987). 
The most immediate and perhaps one of the most 
significant results of Our Common Future was the 
organization of the UN Conference on Environment 
and Development (UNCED), also known as the 
Earth Summit, which gathered many heads of 
state in Rio de Janeiro in 1992. Not only did this 
meeting bring together 108 government leaders, 
more than 2 400 representatives from non-governmental 
organizations (NGOs) attended, and 
17 000 people participated in a parallel NGOs 
event. The Earth Summit strengthened interaction 
among governments, NGOs and scientists, 
and fundamentally changed attitudes towards 
governance and the environment. Governments 
were encouraged to rethink the concept of 
economic development, and to find ways to halt the 
destruction of natural resources and reduce pollution 
of the planet. 
The summit resulted in several important steps 
towards sustainable development. Through the 
adoption of the Rio Declaration and Agenda 21, 
it helped formalize an international institutional 
framework to implement the ideas highlighted 
in Our Common Future. The Rio Declaration 
contains 27 principles that nations agreed to 
follow to achieve the goals articulated by the
Brundtland Commission. Key commitments in the 
Rio Declaration included integration of environment 
and development in decision making, provision for 
polluters to pay for costs of pollution, recognition 
of common but differentiated responsibilities, and 
application of the precautionary approach to 
decision making. 
Agenda 21 articulated a comprehensive plan 
of action towards sustainable development. It 
contains 40 chapters, which can be divided into 
four main areas: 
® social and economic issues, such as poverty, 
human health and population; 
® conservation and management of natural resources 
including the atmosphere, forests, biological 
diversity, wastes and toxic chemicals; 
® the role of nine major groups in implementing the 
sustainable development agenda (local authorities, 
women, farmers, children and youth, indigenous 
peoples, workers and trade unions, NGOs, 
the scientific and technological community, and 
business and industry); and 
® means of implementation, including technology 
transfer, financing, science, education and public 
information. 
Embedded in these four main areas of Agenda 
21 are the environmental challenges, as well as 
the broad governance issues highlighted in the 
Brundtland Commission report. As the blueprint 
for sustainable development, Agenda 21 remains 
the most significant non-binding instrument in the 
environmental field (UNEP 2002). 
Funding for the implementation of Agenda 21 was 
to be obtained from the Global Environment Facility 
(GEF). As a partnership involving the UNEP, UNDP 
and World Bank, GEF was established the year 
before the Earth Summit to mobilize resources for 
projects that seek to protect the environment. Since 
1991, the GEF has provided US$6.8 billion in 
grants, and generated more than US$24 billion in 
co-financing from other sources to support about 
2 000 projects that produce global environmental 
benefits in more than 160 developing countries and 
countries with economies in transition. GEF funds 
are contributed by donor countries, and in 2006, 
32 countries pledged a total of US$3.13 billion to 
fund various environment-related initiatives over four 
years (GEF 2006). 
8 SECTION A: OVERVIEW 
The turn of the century brought a sense of 
urgency to attempts to address environment and 
development challenges. World leaders sought to 
ensure a world free from want. In the Millennium 
Declaration, adopted in 2000, world leaders 
committed to free their people from the “threat of 
living on a planet irredeemably spoilt by human 
activities, and whose resources would no longer 
be sufficient for their needs” (UN 2000). The 
Millennium Summit, adopted the declaration 
and created time-bound goals and targets – the 
Millennium Development Goals (MDGs) – to better 
human well-being. 
Two years after the Millennium Declaration and a 
decade after the Rio Earth Summit, world leaders 
reaffirmed sustainable development as a central goal 
on the international agenda at the 2002 Johannesburg 
World Summit on Sustainable Development (WSSD). 
More than 21 000 participants attended the 
summit, along with representatives of more than 191 
governments. The UN Secretary-General designated 
five priority areas for discussion: water, including 
sanitation, energy, health, agriculture and biodiversity. 
These became to be known by the acronym WEHAB. 
These issues can also be traced back to initiatives such 
as the Brundtland Commission. The WSSD outcomes 
include the Johannesburg Declaration on Sustainable 
Development, and a 54-page plan of implementation. 
World leaders committed themselves, “to expedite 
the achievement of the time-bound, socio-economic 
and environmental targets” contained within the Plan 
of Implementation (Johannesburg Declaration on 
Sustainable Development). This historic summit also 
achieved new commitments on water and sanitation, 
poverty eradication, energy, sustainable production 
and consumption, chemicals, and management of 
natural resources (UN 2002). 
The last 20 years has also seen a growth in the 
number of scientific assessments, such as the 
Intergovernmental Panel on Climate Change, the 
Millennium Ecosystem Assessment and the Global 
Environment Outlook. The Intergovernmental Panel on 
Climate Change was established in 1988 to assess 
on an objective, open and transparent basis the 
scientific, technical and socio-economic information 
relevant to climate change. In 2007, the IPCC 
released its Fourth Assessment Report. The Millennium 
Ecosystem Assessment was called for by the then 
UN Secretary-General Kofi Annan, to assess the
ENV I RONMENT FOR DE V E LOPMENT 9 
consequences of ecosystem change for human well-being. 
These scientific assessments reflect the work 
of thousands of experts worldwide, and have led to 
greater understanding of environmental problems. 
As a result of the conferences and assessments 
highlighted above, a diversity of multilateral 
environmental agreements (MEAs) have been adopted 
(see Figure 1.1), and these and several others are 
analysed in relevant chapters throughout this report. 
The Convention on Biological Diversity (CBD) was 
signed by 150 government leaders at the Rio Earth 
Summit. The CBD sets out commitments for conserving 
biodiversity, the sustainable use of its components, 
and fair and equitable sharing of its benefits. The 
Cartagena Protocol on Biosafety is based on the 
precautionary approach from the Rio Declaration. 
Principle 15 of the Rio Declaration states that, “where 
there are threats of serious and irreversible damage 
lack of full scientific certainty shall not be used as 
a reason for postponing cost effective measures to 
prevent biological degradation” (UNGA 1992). The 
Protocol promotes biosafety in the handling, transfer 
and use of living modified organisms. 
Two agreements that have drawn significant attention 
during the last 20 years are the Montreal Protocol to 
the Vienna Convention on Substances that Deplete 
the Ozone Layer and the Kyoto Protocol to the 
UN Framework Convention on Climate Change. 
The Montreal Protocol, which became effective in 
1989 and had 191 parties at the beginning of 
2007, has helped decrease or stabilize atmospheric 
concentrations of many of the ozone-depleting 
substances, including chlorofluorocarbons. The protocol 
is regarded as one of the most successful international 
agreements to date. By contrast, despite the urgency 
of climate change, it has been much more difficult to 
get some countries responsible for significant emissions 
of greenhouse gases to ratify the Kyoto Protocol. 
Environmental governance has changed since the 
Brundtland Commission. Today, a broader scope of 
issues related to environment and development are 
discussed. The issues of trade, economic development, 
good governance, transfer of technology, science and 
education policies, and globalization, which links 
them together, have become even more central to 
sustainable development. 
Different levels of government participate in 
environmental policy. The post-WCED period saw a 
strong increase in sub-national and local government 
action, for example, through local Agenda 21 
processes. The Johannesburg Plan of Implementation 
stressed that the role of national policies and 
development strategies “cannot be overemphasized.” 
It also strengthened the role of the regional level, 
Figure 1.1 Ratification of major multilateral environmental agreements 
Source: GEO Data Portal, 
compiled from various MEA 
secretariats 
Number of parties 
200 
175 
125 
75 
50 
25 
0 
1971 
2007 
100 
1981 
Basel 
CBD 
CITES 
CMS 
World Heritage 
Kyoto 
1979 
1983 
1975 
Ozone 
1985 
2003 
1999 
1989 
1995 
1987 
1991 
1997 
2001 
1993 
2005 
1997 
Ramsar 
Rotterdam 
Stockholm 
UNCCD 
UNCLOS 
UNFCCC 
Cartagena 
150 
1973
for example by giving the regional UN economic 
commissions new tasks, and establishing a regional 
preparation process for the Commission on Sustainable 
Development (CSD) (UN 2002). 
The number of non-governmental stakeholders involved 
in environmental governance has grown considerably, 
with organizations playing key roles from local to 
global levels. NGOs and advocacy groups devoted 
to public interest and environmental causes have 
multiplied exponentially, particularly in countries 
undertaking democratic transitions (Carothers and 
Barndt 2000). 
The private sector should also take action to help 
protect the environment. Even though business was 
“given little attention by the WCED …, more boards 
and executive committees are trying to consider all 
dimensions of their impacts at once, on the same 
agenda, in the same room” (WBCSD 2007). As 
consumer demand for “green” products arose, 
some businesses developed voluntary environmental 
codes, or followed codes developed by non-governmental 
Box 1.1 Environment as the foundation for development 
10 SECTION A: OVERVIEW 
organizations and governments 
(Prakash 2000). Other companies began to monitor 
and report on their sustainability impacts. A study 
by eight corporate leaders on what business 
success would look like in the future concluded 
that it would be tied to helping society cope 
with challenges such as poverty, globalization, 
environmental decline and demographic change 
(WBCSD 2007). 
Finally, decision making is increasingly participatory. 
Stakeholder groups interact with each other and 
with governments through networks, dialogues and 
partnerships. Interaction among groups at local, 
national and global levels was institutionalized in 
the action plans of UNCED and WSSD. Chapter 37 
of Agenda 21 urged countries to involve all possible 
interest groups in building national consensus on 
Agenda 21 implementation, and Chapter 28 
encouraged local authorities to engage in dialogue 
with their citizens. 
Environment as the foundation for development 
Before the Brundtland Commission, “development 
progress” was associated with industrialization, 
and measured solely by economic activity and 
increases in wealth. Environmental protection 
was perceived by many as an obstacle to 
development. However, Our Common Future 
recognized “environment or development” as a 
false dichotomy. Focus shifted to “environment 
and development,” and then to “environment for 
development (see Box 1.1).” Principle 1 of Agenda 21 
states: “Human beings are at the centre of concerns for 
sustainable development. They are entitled to a healthy 
and productive life in harmony with nature.” 
The normative framework for human development is 
reflected by the MDGs (UNDP 2006). In signing on to 
the MDGs, nations explicitly recognized that achieving 
Goal 7 on environmental sustainability is key to 
achieving poverty eradication. However, environmental 
issues are not highly integrated into other MDGs 
(UNDP 2005a). A healthy environment is essential for 
achieving all the goals (see Table 1.1). To achieve real 
progress, the interlinkages between MDG 7 and the 
other MDGs need to be acknowledged and integrated 
into all forms of planning. 
While a healthy environment can support 
development, the relationship is not always reciprocal. 
Many alternative views exist on the benefits and 
disadvantages of modern development (Rahnema 
1997). It has been argued that development is 
destructive, even violent, to nature (Shiva 1991). As 
GEO-4 illustrates, past development practices have 
often not been beneficial to the environment. However, 
opportunities exist to make development sustainable. 
Environmental degradation due to development raises 
deep ethical questions that go beyond economic 
Development is the process of furthering people’s well-being. Good development entails: 
® increasing the asset base and its productivity; 
® empowering poor people and marginalized communities; 
® reducing and managing risks; and 
® taking a long-term perspective with regard to intra- and intergenerational equity. 
The environment is central to all four of these requirements. Long-term development 
can only be achieved through sustainable management of various assets: financial, 
material, human, social and natural. Natural assets, including water, soils, plants 
and animals, underpin the livelihoods of all people. At the national level, natural 
assets account for 26 per cent of the wealth of low-income countries. Sectors such 
as agriculture, fishery, forestry, tourism and minerals provide important economic 
and social benefits to people. The challenge lies in the proper management of these 
resources. Sustainable development provides a framework for managing human and 
economic development, while ensuring a proper and optimal functioning over time 
of the natural environment. 
Sources: Bass 2006, World Bank 2006a
Livelihood strategies and food security of the poor often depend directly on healthy ecosystems, and the diversity of goods 
and ecological services they provide. Natural capital accounts for 26 per cent of the wealth of low-income countries. 
Climate change affects agricultural productivity. Ground-level ozone damages crops. 
ENV I RONMENT FOR DE V E LOPMENT 11 
Table 1.1 Links between the environment and the Millennium Development Goals 
Millennium Development Goal Selected environmental links 
1. Eradicate extreme poverty and 
hunger 
cost-benefit ratios. The question of justice is perhaps 
the greatest moral question emerging in relation to 
environmental change and sustainable development. 
Growing evidence indicates that the burden 
of environmental change is falling far from the 
greatest consumers of environmental resources, 
who experience the benefits of development. 
Often, people living in poverty in the developing 
world, suffer the negative effects of environmental 
degradation. Furthermore, costs of environmental 
degradation will be experienced by humankind 
in future generations. Profound ethical questions 
are raised when benefits are extracted from the 
environment by those who do not bear the burden. 
Barriers to sustainable development 
Despite changes in environmental governance, 
and greater understanding of the links between 
environment and development, real progress 
towards sustainable development has been slow. 
Many governments continue to create policies 
concerned with environmental, economic and 
social matters as single issues. There is a continued 
failure to link environment and development in 
decision making (Dernbach 2002). As a result, 
development strategies often ignore the need to 
maintain the very ecosystem services on which 
long-term development goals depend. A notable 
example, made apparent in the aftermath of 
2. Achieve universal primary 
education 
Cleaner air will decrease the illnesses of children due to exposure to harmful air pollutants. As a result, they will miss fewer 
days of school. 
Water-related diseases such as diarrhoeal infections cost about 443 million school days each year, and diminish learning 
potential. 
3. Promote gender equality, and 
empower women 
Indoor and outdoor air pollution is responsible for more than 2 million premature deaths annually. Poor women are 
particularly vulnerable to respiratory infections, as they have high levels of exposure to indoor air pollution. 
Women and girls bear the brunt of collecting water and fuelwood, tasks made harder by environmental degradation, such as 
water contamination and deforestation. 
4. Reduce child mortality Acute respiratory infections are the leading cause of death in children. Pneumonia kills more children under the age of 5 than 
any other illness. Environmental factors such as indoor air pollution may increase children’s susceptibility to pneumonia. 
Water-related diseases, such as diarrhoea and cholera, kill an estimated 3 million people/year in developing countries, 
the majority of whom are children under the age of five. Diarrhoea has become the second biggest killer of children, with 
1.8 million children dying every year (almost 5 000/day). 
5. Improve maternal health Indoor air pollution and carrying heavy loads of water and fuelwood adversely affect women’s health, and can make women 
less fit for childbirth and at greater risk of complications during pregnancy. 
Provision of clean water reduces the incidence of diseases that undermine maternal health and contribute to maternal 
mortality. 
6. Combat major diseases Up to 20 per cent of the total burden of disease in developing countries may be associated with environmental risk factors. 
Preventative environmental health measures are as important and at times more cost-effective than health treatment. 
New biodiversity-derived medicines hold promises for fighting major diseases. 
7. Ensure environmental 
sustainability 
Current trends in environmental degradation must be reversed in order to sustain the health and productivity of the world’s 
ecosystems. 
8. Develop a global partnership 
for development 
Poor countries and regions are forced to exploit their natural resources to generate revenue and make huge debt repayments. 
Unfair globalization practices export their harmful side-effects to countries that often do not have effective governance 
regimes. 
Source: Adapted from DFID and others 2002, UNDP 2006, UNICEF 2006
the 2005 Hurricane Katrina, is the failure of some 
government agencies to see the link between 
destruction of coastal wetlands and the increased 
vulnerability of coastal communities to storms (Travis 
2005, Fischetti 2005). For many, acknowledging 
that environmental change could endanger future 
human well-being is inconvenient, as it requires an 
uncomfortable level of change to individual and 
working lives (Gore 2006). 
International negotiations on solutions to global 
environmental problems have frequently stalled 
over questions of equity (Brown 1999). For instance, 
in the case of climate change, international 
negotiations have slowed down over the question 
on how to share responsibilities and burden among 
nations, given different historic and current levels of 
national emissions. 
Providing widespread participation in sustainable 
development decision making called for by 
Agenda 21 has also raised significant challenges. 
The enormous diversity of issues that need to be 
considered in sustainable development policy 
making, together with aspirations for transparency, 
12 SECTION A: OVERVIEW 
make public participation design daunting. If 
participation is treated superficially, and embodied 
merely as a quota of specified groups in decision 
making processes, it could easily be no more than 
“lip service.” The task of designing modern, cross-cutting, 
transparent, evidence-based interdisciplinary 
decision making is not only conceptually 
challenging, but also necessitates a huge increase 
in local capacity for democracy and decision 
making (MacDonald and Service 2007). 
Many social, economic and technological 
changes described later in this chapter have made 
implementation of the recommendations in Our 
Common Future difficult. As also illustrated in other 
chapters, changes such as a growing population and 
increased consumption of energy have had a huge 
impact on the environment, challenging society’s ability 
to achieve sustainable development. 
Finally, the nature of the environmental problems 
has influenced the effectiveness of past responses. 
Environmental problems can be mapped along a 
continuum from “problems with proven solutions” to 
“less known emerging (or persistent) problems” (Speth 
2004). With problems with proven solutions, the cause-and- 
effect relationships are well known. The scale tends 
to be local or national. Impacts are highly visible and 
acute, and victims are easily identified. During the past 
20 years, workable solutions have been identified for 
several such problems, for example industrial air and 
water pollution, local soil erosion, mangrove clearance 
for aquaculture, and vehicle exhaust emissions. 
However, progress has been limited on harder to 
manage environmental issues, which can also be 
referred to as “persistent” problems (Jänicke and 
Volkery 2001). These are deeply rooted structural 
problems, related to the ways production and 
consumption are conducted at the household, national, 
regional and global levels. Harder to manage 
problems tend to have multiple dimensions and be 
global in scale. Some of the basic science of cause-and- 
effect relationships is known, but often not enough 
to predict when a tipping point or a point of no return 
will be reached. There is often a need to implement 
measures on a very large-scale. Examples of such 
problems include global climate change, persistent 
organic pollutants and heavy metals, ground level 
ozone, acid rain, large-scale deterioration of fisheries, 
extinction of species, or introductions of alien species. 
Women and girls bear the brunt 
of collecting fuelwood, tasks 
made harder by environmental 
degradation. 
Credit: Christian Lambrechts
ENV I RONMENT FOR DE V E LOPMENT 13 
Awareness of the nature of an environmental problem 
provides a basis for creating strategies, targeting 
efforts, and finding and implementing a sustainable 
solution. Possible solutions to different types of 
environmental problems are introduced in the last 
section of this chapter, highlighted in the rest of the 
report, and discussed further in Chapter 10. 
HUMAN WELL-BEING AND THE 
ENVIRONMENT 
For sustainable development to be achieved, links 
between the environment and development must 
be examined. It is also important to consider the 
end point of development: human well-being. The 
evolution of ideas on development has made the 
concept of human well-being central to the policy 
debate. Human well-being is the outcome of 
development. Human well-being and the state of 
the environment are strongly interlinked. Establishing 
how environmental changes have impacts on 
human well-being, and showing the importance of 
environment for human well-being, are among the 
core objectives of this report. 
Defining human well-being 
Defining human well-being (see Box 1.2) is not 
easy, due to alternative views on what it means. 
Simply put, human well-being can be classified 
according to three views, each of which has 
different implications for the environment: 
® The resources people have, such as money 
and other assets. Wealth is seen as conducive 
to well-being. This view is closely linked to the 
concept of weak sustainability, which argues 
that environmental losses can be compensated 
for by increases in physical capital (machines) 
(Solow 1991). The environment can only 
contribute to development as a means to 
promote economic growth. 
® How people feel about their lives (their 
subjective views). Individuals’ assessments of 
their own living conditions take into account 
the intrinsic importance that environment has 
for life satisfaction. According to this view, 
people value the environment for its traditional 
or cultural aspects (Diener 2000, Frey and 
Stutzer 2005). 
® What people are able to be and to do. 
This view focuses on what the environment 
allows individuals to be and to do (Sen 
1985, Sen 1992, Sen 1999). It points out 
that the environment provides the basis for 
many benefits, such as proper nourishment, 
avoiding unnecessary morbidity and 
premature mortality, enjoying security and 
self-respect, and taking part in the life of the 
community. The environment is appreciated 
beyond its role as income generator, and its 
impacts on human well-being are seen as 
multidimensional. 
Human well-being is the extent to which individuals have the ability and 
the opportunity to live the kinds of lives they have reason to value. 
People’s ability to pursue the lives that they value is shaped by a 
wide range of instrumental freedoms. Human well-being encompasses 
personal and environmental security, access to materials for a good 
life, good health and good social relations, all of which are closely 
related to each other, and underlie the freedom to make choices and 
take action: 
® Health is a state of complete physical, mental and social well-being, 
and not merely the absence of disease or illness. Good 
health not only includes being strong and feeling well, but also 
freedom from avoidable disease, a healthy physical environment, 
access to energy, safe water and clean air. What one can be and 
do include among others, the ability to keep fit, minimize health-related 
stress, and ensure access to medical care. 
® Material needs relate to access to ecosystem goods-and-services. 
The material basis for a good life includes secure and adequate 
livelihoods, income and assets, enough food and clean water at all 
times, shelter, clothing, access to energy to keep warm and cool, 
and access to goods. 
® Security relates to personal and environmental security. It includes 
access to natural and other resources, and freedom from violence, 
crime and wars (motivated by environmental drivers), as well as 
security from natural and human-caused disasters. 
® Social relations refer to positive characteristics that define 
interactions among individuals, such as social cohesion, 
reciprocity, mutual respect, good gender and family relations, and 
the ability to help others and provide for children. 
Increasing the real opportunities that people have to improve their 
lives requires addressing all these components. This is closely linked 
to environmental quality and the sustainability of ecosystem services. 
Therefore, an assessment of the impact of the environment on 
individuals’ well-being can be done by mapping the impact of the 
environment on these different components of well-being. 
Box 1.2 Human well-being 
Sources: MA 2003, Sen 1999
The evolution of these ideas has progressed from 
the first to the third, with increasing importance 
being given to the real opportunities that people 
have to achieve what they wish to be and to do. 
This new understanding of human well-being has 
several important aspects. First, multidimensionality 
is viewed as an important feature of human well-being. 
14 SECTION A: OVERVIEW 
Consequently, the impact of the environment 
on human well-being is seen according to many 
different dimensions. 
Second, autonomy is considered a defining feature 
of people, and of well-being. Autonomy can be 
defined broadly as allowing people to make 
individual or collective choices. In other words, 
to know whether an individual is well requires 
considering his or her resources, subjective views, 
and the ability to choose and act. This concept 
of human well-being highlights the importance 
of understanding whether individuals are simply 
passive spectators of policy interventions, or, in 
fact, active agents of their own destiny. 
Context of human well-being 
The potential for individuals, communities and nations 
to make their own choices, and maximize opportunities 
to achieve security and good health, meet material 
needs and maintain social relations is affected by 
many interlinked factors, such as poverty, inequality 
and gender. It is important to note how these factors 
relate to each other, and to the environment. 
Poverty and inequality 
Poverty is understood as a deprivation of basic 
freedoms. It implies a low level of well-being, with 
such outcomes as poor health, premature mortality 
and morbidity, and illiteracy. It is usually driven by 
inadequate control over resources, discrimination 
(including by race or gender), and lack of access 
to material assets, health care and education 
(UN 2004). 
Inequality refers to the skewed distribution of an 
object of value, such as income, medical care or 
clean water, among individuals or groups. Unequal 
access to environmental resources remains an 
important source of inequality among individuals. 
Equity is the idea that a social arrangement 
addresses equality in terms of something of value. 
Distributive analysis is used to assess features of 
human well-being that are unequally distributed 
among individuals according to arbitrary factors, 
such as gender, age, religion and ethnicity. When 
an analysis of this distribution focuses on its lower 
end, it refers to poverty. 
Mobility 
When seen in a dynamic perspective, inequality and 
poverty are better understood through the concepts 
of social mobility and vulnerability. Mobility relates to 
the ability of people to move from one social group, 
class or level to another. Environmental degradation 
may be responsible for locking individuals within low-mobility 
paths, limiting opportunities to improve their 
own well-being. 
Vulnerability 
Vulnerability involves a combination of exposure and 
sensitivity to risk, and the inability to cope or adapt to 
environmental change. Most often, the poor are more 
vulnerable to environmental change. Broad patterns 
of vulnerability to environmental and socio-economic 
changes can be identified so that policy-makers 
can respond, providing opportunities for reducing 
Individuals’ assessments of their 
own living conditions take into 
account the intrinsic importance 
that the environment has for life 
satisfaction. 
Credit: Mark Edwards/Still Pictures
Box 1.3 Ecosystem services 
Ecosystem services include provisioning services, such as food and water; regulating 
services, such as flood and disease control; cultural services, such as spiritual, 
recreational and cultural benefits; and supporting services, such as nutrient cycling that 
maintain the conditions for life on Earth (see Table 5.2 in Chapter 5 for details). 
ENV I RONMENT FOR DE V E LOPMENT 15 
vulnerability, while protecting the environment. Chapter 
7 assesses the vulnerability of the human-environment 
system to multiple stresses (drivers and pressures). 
Gender inequality 
An analysis of distributive impacts of the environment 
on human well-being cannot ignore features such as 
gender. Gender inequality is one of the most persistent 
inequalities in both developed and developing 
countries, with the majority of people living in poverty 
being women (UNDP 2005b). Women and girls often 
carry a disproportionate burden from environmental 
degradation compared to men. Understanding the 
position of women in society, and their relationship 
with the environment is essential for promoting 
development. In many cases, women and girls assume 
greater responsibilities for environmental management, 
but have subordinate positions in decision making 
(Braidotti and others 1994). Women need to be at 
the centre of policy responses (Agarwal 2000). At the 
same time, it is important to avoid stereotyping these 
roles, and to base responses on the complexities of 
local realities (Cleaver 2000). 
Environmental change and human well-being 
One of the main findings of the Millennium Ecosystem 
Assessment is that the relationship between human 
well-being and the natural environment is mediated 
by services provided by ecosystems (see Box 1.3). 
Changes to these services, as a result of changes 
in the environment, affect human well-being through 
impacts on security, basic material for a good life, 
health, and social and cultural relations (MA 2003). 
All people – rich and poor, urban and rural, and in all 
regions – rely on natural capital. 
The world’s poorest people depend primarily on 
environmental goods-and-services for their livelihoods, 
which makes them particularly sensitive and vulnerable 
to environmental changes (WRI 2005). Furthermore, 
many communities in both developing and developed 
countries derive their income from environmental 
resources, which include fisheries, non-timber forest 
products and wildlife. 
Health 
Shortly before the publication of Our Common 
Future, the nuclear accident at Chernobyl illustrated 
the catastrophic impact pollution can have on health. 
Twenty years later, as victims of Chernobyl still 
struggle with disease, the health of countless other 
people around the world continues to be affected by 
human-induced changes to the environment. Changes 
The relationship between human 
well-being and the natural 
environment is influenced by 
services provided by ecosystems. 
Credit: Joerg Boethling/Still Pictures 
Source: MA 2005a
affecting provisioning services, including water, can 
influence human health. Changes affecting regulating 
services influence health via the distribution of disease 
transmitting insects or pollutants in water and air (MA 
2003). Almost one-quarter of all diseases are caused 
by environmental exposure (WHO 2006). 
As described in Chapter 2, urban air pollution is one of 
the most widespread environmental problems, affecting 
health in almost all regions of the world. While 
Sources: Bell and others 2004, Brown 2006, Goodall 2005, Fa and others 2007, Karesh and others 2005, Leroy and others 2004, Li and others 2005, Peiris and others 2004, 
Peterson 2003, Wolfe and others 2004, Wolfe and others 2005 
16 SECTION A: OVERVIEW 
air pollution has decreased in many industrialized 
countries, it has increased in other regions, particularly 
in Asia. Here, rapid population growth, economic 
development and urbanization have been associated 
with increasing use of fossil fuels, and a deterioration 
of air quality. WHO estimates that more than 1 billion 
people in Asian countries are exposed to air pollutant 
levels exceeding their guidelines (WHO 2000). In 
2002, WHO estimated that more than 800 000 
people died prematurely due to PM10 (particulate 
The bushmeat trade in Central Africa, and wildlife markets in Asia are 
examples of activities that both have impacts on the environment, and 
carry risk of disease emergence. In Viet Nam, the illegal trade in wildlife 
currently generates US$20 million/year. Wild meat is a critical source 
of protein and income for forest dwellers and rural poor. However, 
commercial demand for wild meat has been growing as a result of urban 
consumption, from wildlife restaurants and medicine shops, but also 
from markets in neighbouring countries. Rates of wildlife harvesting are 
unsustainable, and threaten species such as the small-toothed palm civet 
with extinction. 
In wildlife markets, mammals, birds and reptiles come in contact with 
dozens of other species and with countless numbers of people, increasing 
opportunity for disease transmission. Not surprisingly, during the 2003 
Sudden Acute Respiratory Syndrome (SARS) epidemic, several of the 
early patients in Guangdong Province, China, worked in the sale or 
preparation of wildlife for food. The disease may have first spread to 
humans from civet cats or bats in local wildlife markets. Through human 
air travel, SARS quickly spread to 25 countries across five continents. 
With more than 700 million people travelling by air annually, disease 
outbreaks can easily grow into worldwide epidemics. 
It is estimated that every year between 1.1 and 3.4 million tonnes of 
undressed wild animal biomass, or bushmeat, are consumed by people 
living the Congo Basin. The wild meat trade, commercial hunting of wild 
animals for meat, has decimated endangered populations of long-lived 
species such as chimpanzees. Trade is global in nature, and primate meat 
has even been found in markets in Paris, London, Brussels, New York, 
Chicago, Los Angeles, Montreal and Toronto. Contact with primate blood 
and bodily fluids during hunting and butchering has exposed people to 
novel viruses. Between 2000 and 2003, 13 of 16 Ebola outbreaks in 
Gabon and the Republic of Congo resulted from the handling of gorilla or 
chimpanzee carcasses. A recent study documents simian foamy virus (SFV) 
and human T-lymphotic (HTLV) viruses in individuals engaged in bushmeat 
hunting in rural Cameroon. 
Box 1.4 Wild meat trade 
Commercial demand for wild meat has been growing and rates of wildlife harvesting are unsustainable. 
Credit: Lise Albrechtsen
Box 1.5 Material well-being from fisheries 
ENV I RONMENT FOR DE V E LOPMENT 17 
matter with a diameter less than 10 micrometers) 
outdoor pollution and 1.6 million due to PM10 indoor 
air pollution (WHO 2002) (see Chapter 2). 
Chapter 4 highlights how the overexploitation and 
pollution of freshwater ecosystems – rivers, lakes, 
wetlands and groundwater – has direct impacts on 
human well-being. Although access to clean water 
and sanitation has improved, in 2002 more than 
1.1 billion people lacked access to clean water, 
and 2.6 billion lacked access to improved sanitation 
(WHO and UNICEF 2004). Annually, 1.8 million 
children die from diarrhoea, making the disease the 
world’s second biggest killer of children (UNDP 2006). 
Many heavy metals, such as mercury and lead, are 
found in water and sediments, and are a major concern 
as they can accumulate in the tissues of humans and 
other organisms (UNESCO 2006). Numerous activities 
contribute to heavy metal contamination. Burning coal, 
incineration, urban and agricultural run-off, industrial 
discharges, small-scale industrial activities, mining, and 
landfill leakages are among the main ones described in 
Chapters 2, 3 and 4. 
Changes in the environment have also resulted in 
the emergence of diseases. Since 1980, more than 
35 infectious diseases have emerged or taken on 
new importance. These include previously unknown, 
emerging diseases, such as HIV, SARS and avian 
influenza (H5N1), as well as diseases once thought 
controllable, such as dengue fever, malaria and 
bubonic plague (Karesh and others 2005, UNEP 
2005a). Human-induced changes to the environment, 
such as climate change, land use change and 
interaction with wildlife (see Box 1.4), have driven this 
recent epidemiological transition (McMichael 2001, 
McMichael 2004). Growing human contact with 
wildlife, caused by population pressure on remaining 
relatively undisturbed environmental resources, increases 
the opportunity for pathogen exchange (Wolfe and 
others 1998). Globalization, in turn, has an effect 
on disease emergence as disease agents have the 
opportunity to move into new niches, and meet new, 
vulnerable populations. A recent UNEP report on Avian 
Influenza and the Environment states: “If the transfer of 
Asian lineage H5N1 between domestic flocks and wild 
birds is to be reduced, it will become essential to take 
measures to minimize their contact. Restoring wetland 
health will reduce the need for migrating wild birds to 
share habitat with domestic poultry” (UNEP 2006). 
Material needs 
People depend on natural resources for their basic 
needs, such as food, energy, water and housing. 
In many communities, particularly in developing 
countries, environmental resources, including 
fisheries, timber, non-timber forest products and 
wildlife, directly contribute to income and other 
material assets required to achieve a life that one 
values. The ability to meet material needs is strongly 
linked to the provisioning, regulating and supporting 
services of ecosystems (MA 2003). 
More than 1.3 billion people depend on fisheries, 
forests and agriculture for employment – close to half 
of all jobs worldwide (see Box 1.5) (FAO 2004a). In 
Asia and the Pacific, small-scale fisheries contributed 
25 per cent to the total fisheries production of 
Malaysia, the Philippines, and Thailand for the decade 
ending in 1997 (Kura and others 2004). In Africa, 
more than 7 in 10 people live in rural areas, with 
most engaged in resource-dependent activities (IFAD 
2001). The corresponding small-scale production 
accounts for a significant percentage of the GDP in 
many African countries (IFPRI 2004). Moreover, small-scale 
agriculture accounts for more than 90 per cent 
of Africa’s agricultural production (Spencer 2001). 
A study of households in the Masvingo province in 
southeast Zimbabwe indicates that 51 per cent of 
incomes are from agriculture, and that the total income 
from the environment averages 66 per cent (Campbell 
and others 2002). Where resources are degraded, 
livelihoods are placed at risk. Forest loss may reduce 
The fisheries sector plays an important role in material well-being, providing income 
generation, poverty alleviation and food security in many parts of the world. Fish 
is an important protein source, especially in the developing world, providing more 
than 2.6 billion people with at least 20 per cent of their average per capita animal 
protein intake. The world’s population growth outpaced that of total fish supply and 
FAO projections indicate that a global shortage is expected (see Chapter 4). 
While fish consumption increased in some regions, such as South East Asia, Europe and 
North America, it declined in others, including sub-Saharan Africa and Eastern Europe. 
The collapse of the Canadian east coast cod fishery in the late 1980s had devastating 
impacts on local fishing communities, and illustrates that developed countries are not 
immune to the economic implications of mismanaging natural resources. It resulted in 
unemployment for 25 000 fishers and 10 000 other workers (see Box 5.2 and Figure 
7.17 in Chapters 5 and 7 respectively). 
Sources: Delgado and others 2003, FAO 2004b, Matthews 1995
the availability of food, energy resources and other 
forest products, which, in many communities, support 
trade and income earning opportunities. 
Increasing evidence shows that investment in ecosystem 
conservation, such as watershed management, results 
in increased income for the rural poor. In the Adgaon 
watershed in India, the annual days of employment 
(wage labour) per worker increased from 75 days 
before watershed rehabilitation to 200 days after 
restoration was completed (Kerr and others 2002). In 
Fiji, strengthening the traditional “no-take” management 
system to promote recovery of marine life has resulted 
in a 35–43 per cent increase in income over a 
period of three years (see Box 7.13) (WRI 2005). 
In a pioneering people-led watershed management 
project in India, the implementation of a participatory 
restoration scheme led to halving the distance to 
the water table, a doubling of land under irrigation, 
and an increase in the total agricultural income of 
the village from about US$55 000 in 1996, before 
watershed regeneration, to about US$235 000 in 
2001 (D’Souza and Lobo 2004, WRI 2005). 
Security 
Security incorporates economic, political, cultural, 
social and environmental aspects (Dabelko and others 
2000). It includes freedom from threats of bodily 
harm, and from violence, crime and war. It means 
South Pacific 
Western Indian Ocean 
millions 
1.8 
1.4 
1.0 
18 SECTION A: OVERVIEW 
having stable and reliable access to resources, the 
ability to be secure from natural and human disasters, 
and the ability to mitigate and respond to shocks and 
stresses. Environmental resources are a critical part 
of the livelihoods of millions of people, and when 
these resources are threatened through environmental 
change, people’s security is also threatened. “At the 
centre of sustainable development is the delicate 
balance between human security and the environment” 
(CHS 2006). 
The Earth has shown clear signs of warming 
over the past century. Eleven of the last 12 years 
(1995–2006) rank among the 12 warmest 
years in the instrumental record of global surface 
temperature (since 1850) (IPCC 2007). As 
Chapter 2 describes, climate change is very likely 
to affect ecological regulating services, resulting 
in increased frequency and intensity of extreme 
weather hazards in many regions around the globe 
(IPCC 2007), and greater insecurity for much 
of the world’s population (Conca and Dabelko 
2002). The impacts of extreme weather events will 
fall disproportionately upon developing countries, 
such as Small Island Developing States (SIDS) 
(see Figure 1.2), as well as on the poor in all 
countries (IPCC 2007). During Hurricane Katrina 
in the United States in 2005, impoverished people 
without access to private transportation were unable 
Figure 1.2 Number of people affected by disasters of natural origin in SIDS 
Note: Excluding earthquakes, 
insect infections and volcanic 
eruptions. 
Source: GEO Data Portal, 
compiled from EM-DAT undated 
2.0 
0 
1987 
0.8 
Caribbean 
1988 
1989 
1990 
1991 
1992 
1993 
1994 
1995 
1996 
1997 
1998 
1999 
2000 
2001 
2004 
2002 
2003 
1.6 
1.2 
0.6 
0.4 
0.2 
3.03 
5.92
ENV I RONMENT FOR DE V E LOPMENT 19 
to leave the city. People in poor health or lacking 
bodily strength were less likely to survive the Indian 
Ocean tsunami in 2004. For example, in villages 
in North Aceh, Indonesia, women constituted up to 
80 per cent of deaths (Oxfam 2005). In Sri Lanka, 
a high mortality rate was also observed among 
other vulnerable groups: children and the elderly 
(Nishikiori and others 2006). 
Environmental change can also affect security 
through changes in provisioning services, which 
supply food and other goods. Scarcity of shared 
resources has been a source of conflict and social 
instability (deSombre and Barkin 2002). Disputes 
over water quantity and quality are ongoing in 
many parts of the world. The apparent degradation 
of Easter Island’s natural resources by its Polynesian 
inhabitants, and the ensuing struggle between clans 
and chiefs, provides a graphic illustration of a 
society that destroyed itself by overexploiting scarce 
resources (Diamond 2005). Natural resources can 
play an important role in armed conflicts. They have 
often been a means of funding war (see Box 1.6). 
Armed conflicts have also been used as a means 
to gain access to resources (Le Billion 2001), and 
they can destroy environmental resources. 
Natural resources, including diamonds and timber, helped fuel civil war 
in Liberia and Sierra Leone during the 1990s. Diamonds were smuggled 
from Sierra Leone into Liberia and onto the world market. In the mid- 
1990s, Liberia’s official diamond exports ranged between US$300 and 
US$450 million annually. These diamonds have been referred to as 
“blood diamonds,” as their trade helped finance rebel groups and the 
continued hostilities. By the end of the war in 2002, more than 50 000 
people had died, 20 000 were left mutilated and three-quarters of the 
population had been displaced in Sierra Leone alone. 
As civil wars raged in Sierra Leone and Liberia, hundreds of thousands 
of refugees fled to safety in Guinea. In 2003, about 180 000 refugees 
resided in Guinea. Between Sierra Leone and Liberia, there is a small strip 
of land belonging to Guinea known as the “Parrot’s Beak,” because of 
the parrot shape contour of the international border between the countries 
(depicted as a black line on both images). This strip is where refugees 
constituted up to 80 per cent of the local population. 
The 1974 image shows small, evenly spread, scattered flecks of 
light green in the dark green forest cover of the Parrot’s Beak and 
surrounding forests of Liberia and Sierra Leone. These flecks are 
village compounds, with surrounding agricultural plots. The dark areas 
in the upper left of the image are most likely burn scars. 
In the 2002 image Parrot’s Beak is clearly visible as a more evenly 
spread light grey and green area surrounded by darker green forest 
of Liberia and Sierra Leone. The light colours show deforestation 
in the “safe area” where refugees had set up camp. Many of the 
refugees integrated into local villages, creating their own family plots 
by cutting more trees. As a result the isolated flecks merged into one 
larger area of degraded forest. The forest devastation is especially 
obvious in the upper left part, where areas that were green in 1974 
now appear grey and brown, also due to expanded logging. 
Box 1.6 Conflict in Sierra Leone and Liberia, and refugee settlement in Guinea 
Sources: Meredith 2005, UNEP 2005b, UNHCR 2006a 
Credit: UNEP 2005b
Insecurity caused by bad governance or war can 
contribute to environmental degradation. Security 
requires the current and future availability of 
environmental goods-and-services, through good 
governance, mechanisms for conflict avoidance and 
resolution, and for disaster prevention, preparedness 
and mitigation (Dabelko and others 2000, Huggins and 
Box 1.7 Chemicals affect Arctic peoples 
Ocean currents 
Surface water circulation 
River inflow 
Note: Rivers and ocean currents are 
important pathways for water-soluble 
contaminants and those that are attached 
to particles in the water. 
Note: Winds provide a fast route for 
contaminants from industrial areas to 
the Arctic especially in winter. 
20 SECTION A: OVERVIEW 
others 2006, Maltais and others 2003). Inequitable 
governance and institutions may prevent people from 
having secure livelihoods, as illustrated by land tenure 
conflicts in Southern Africa (Katerere and Hill 2002), 
and by poor management in Indonesia’s peat swamps 
(Hecker 2005). In both examples, the resource is 
closely linked to local livelihoods, and insecurity is a 
result not so much of scarcity but of unequal access to 
and distribution of these vital resources. In other cases, 
as illustrated in Box 1.6, degradation may result from 
changes in settlement patterns as people are forced to 
flee an area due to hostilities or war. 
It has become clear in recent years that joint 
management on environmental matters is needed to 
facilitate cooperation across societal and international 
boundaries to avoid conflict (Matthew and others 
2002; UNEP 2005b). The case of cooperative 
endeavours to deal with fisheries decline in Lake 
Victoria is an excellent example. Cooperation on water 
management and transnational ecosystems can also 
foster diplomatic habits of consultation and dialogue 
with positive political results, suggesting that human 
and environmental security are very closely linked 
(Dodds and Pippard 2005). 
Social relations 
The environment also affects social relations by 
providing cultural services, such as the opportunity to 
express aesthetic, cultural or spiritual values associated 
with ecosystems (MA 2005a). The natural world 
provides opportunities for observation and education, 
recreation and aesthetic enjoyment, all of which are 
of value to a given society. In some communities, 
the environment underpins the very structure of social 
relations. As described in Chapter 5, many cultures, 
particularly indigenous ones, are deeply interwoven 
with the local environment. 
Climate change is a major concern for SIDS and their 
high cultural diversity; SIDS are imperilled by sea-level 
rise and increases in the intensity and number of storms 
(Watson and others 1997) (see Chapter 7). Tuvalu is 
an example of an island vulnerable to environmental 
change. Even though its culture is strongly related 
to the local environment, the islanders may have 
to consider relocating to other countries to escape 
rising sea level as a result of climate change. Coping 
mechanisms embedded in such cultures might be lost, 
making society less resilient to future natural disasters 
(Pelling and Uitto 2001). 
As described in Chapters 5 and 6, the relationships that indigenous peoples have 
with the environment play an important role in their identity and overall well-being. 
Scientific assessments have detected persistent organic pollutants (POPs) and heavy 
metals in all components of the Arctic ecosystem, including in people. The majority of 
these substances are present in the ecosystems and diets of Arctic peoples as a result of 
choices (such as using the insecticide toxaphene on cotton fields) by industrial societies 
elsewhere. Contaminants reach the Arctic from all over the world through wind, air and 
water currents (see Figure 1.3), entering the food chain. 
Inuit populations in the eastern Canadian Arctic and Greenland have among the highest 
exposures to POPs and mercury from a traditional diet of populations anywhere. A 
sustainable lifestyle, with ancient roots in the harvesting, distribution and consumption of 
local renewable resources, is endangered as a result. 
Sources: Doubleday 1996, Van Oostdam 2005 
Beaufort Gyre Transpolar Drift 
Wind frequencies 
Winter: 25% 
Summer: 5% 
Wind frequencies 
Winter: 15% 
Summer: 5% 
Wind frequencies 
Winter: 40% 
Summer: 10% 
Arctic front, summer 
Arctic front, winter 
Figure 1.3 Pollutants paths to the Arctic 
Credit: AMAP 2002
Figure 1.4 Population by region 
2003 
ENV I RONMENT FOR DE V E LOPMENT 21 
A diet of traditional foods plays a particularly important 
role in the social, cultural, nutritional and economic 
health of indigenous peoples living in the Arctic 
(Donaldson 2002). Hunting, fishing, and the gathering 
of plants and berries are associated with important 
traditional values and practices that are central to their 
identity as indigenous peoples. Their traditional food is 
compromised by environmental contaminants (see Box 
1.7 and Figure 1.3) and climate change (see Chapter 
6), and this affects all dimensions of indigenous well-being. 
The issue becomes magnified in light of the lack 
of accessible, culturally acceptable and affordable 
alternatives. Store food is expensive, and lacks cultural 
significance and meaning. Long-term solutions require 
that Arctic lifestyles be considered when development 
choices are made in industrial and agricultural regions 
around the world (Doubleday 2005). 
DRIVERS OF CHANGE AND PRESSURES 
Environmental changes and the effects on human well-being 
are induced by various drivers and pressures. 
Drivers such as demographic changes, economic 
demand and trade, science and technology, as well 
as institutional and socio-political frameworks induce 
pressures which, in turn, influence the state of the 
environment with impacts on the environment itself, 
and on society and economic activity. Most pressures 
on ecosystems result from, for example, changes in 
emissions, land use and resource extraction. Analyses 
of the linkages shown by the drivers-pressures-state-impacts- 
responses (DSPIR) framework (described in 
the Reader’s Guide to the report) form the foundation 
on which the GEO-4 assessment is constructed. In 
the two decades since the Brundtland Commission, 
these drivers and pressures have changed, often at an 
increasing rate. The result is that the environment has 
changed dramatically. No region has been spared the 
reality of a changing environment, and its immediate, 
short- and long-term impacts on human well-being. 
Population 
Population is an important driver behind environmental 
change, leading to increased demand for food, 
water and energy, and placing pressure on natural 
resources. Today’s population is three times larger than 
it was at the beginning of the 20th century. During 
the past 20 years global population has continued to 
rise, increasing from 5 billion in 1987 to 6.7 billion 
in 2007 (see Figure 1.4), with an average annual 
growth rate of 1.4 per cent. However, large differences 
in growth are evident across regions, with Africa 
billions 
3.5 
3.0 
2.5 
1.5 
1.0 
0.5 
and West Asia recording high growth rates, and the 
European population stabilizing (see Chapter 6 for more 
detail). Although the world population is increasing, the 
rate of increase is slowing (see Box 1.8). 
Forced and economic migrations influence demographic 
changes and settlement patterns, particularly at the 
regional level. There were 190 million international 
migrants in 2005, compared to 111 million in 1985. 
About one-third of migrants in the world have moved 
from one developing country to another, while another 
third have moved from a developing country to a 
developed country (UN 2006). Many migrants are 
refugees, internally displaced or stateless persons. At 
the end of 2005, more than 20.8 million people were 
classified as “of concern” to the UN High Commission 
for Refugees (UNHCR 2006b). These included 
refugees, internally displaced and stateless persons. 
Worldwide refugee numbers have decreased since 
2000, but there has been an upward trend in numbers 
of other displaced groups (UNHCR 2006b). 
The term ecomigrant has been used to describe 
anyone whose need to migrate is influenced 
by environmental factors (Wood 2001). It has 
been claimed that during the mid-1990s up 
to 25 million people were forced to flee as a 
result of environmental change, and as many as 
200 million people could eventually be at risk 
of displacement (Myers 1997). Other analyses 
indicated that while the environment may play a 
role in forced migration, migration is usually also 
linked to political divisions, economic interests and 
ethnic rivalries (Castles 2002). A clear separation 
between factors is often difficult. 
Source: GEO Data Portal, 
compiled from UNPD 2007 
4.0 
0 
1987 
2007 
1989 
1995 
2.0 
1999 
Africa 
Asia and the Pacific 
Europe 
Latin America and the Caribbean 
North America 
West Asia 
1991 
1993 
1997 
2001 
2005
Box 1.8 Demographic transition 
The annual global population growth rate declined from 
1.7 per cent in 1987 to 1.1 per cent in 2007. Significant 
regional variations are analysed in chapter 6. Demographic 
transition, the change from high birth and death rates to 
low birth and death rates, can explain these changes in 
population. As a result of economic development, fertility 
rates are falling in all regions. In the period between 2000 
and 2005, the world recorded a fertility rate of 2.7 children 
per woman, compared to a fertility rate of 5.1 children 
per woman 50 years before. Ultimately, fertility may even 
drop below 2, the replacement rate, leading to a global 
population decline. Some European countries are at this 
stage, and have ageing populations. 
Sources: GEO Data Portal, from UNPD 2007, UNAIDS 2006 
Figure 1.5 Life expectancy by region 
Africa 
Asia and the Pacific 
Europe 
Latin America and the Caribbean 
North America 
West Asia 
Source: GEO Data Portal, 
compiled from UNPD 2007 
Figure 1.6 Urban population by region, per cent of total population 
Source: GEO Data Portal, 
compiled from UNPD 2005 
per cent 
90 
70 
60 
50 
30 
20 
0 
22 SECTION A: OVERVIEW 
1985 
40 
10 
Africa 
Asia and the Pacific 
Europe 
Latin America and the Caribbean 
North America 
West Asia 
80 
Improved health has led to lower mortality rates and 
higher life expectancies in most regions (see Figure 
1.5). However, life expectancy in many parts of 
Africa has decreased during the last 20 years, partly 
as a result of the AIDS pandemic. Around the world, 
more than 20 million people have died since the first 
cases of AIDS were identified in 1981. It is estimated 
that 39.5 million adults and children where living 
with HIV in 2005, of which 24.7 million were in sub- 
Saharan Africa. In hardest-hit countries, the pandemic 
has reduced life expectancy, lessening the number of 
healthy agricultural workers and deepening poverty. 
years 
80 
70 
60 
50 
40 
30 
20 
10 
0 
1985–90 
1990–95 1995–2000 2000–05 
1990 1995 2000 2005 2010 2015 2020 2025
ENV I RONMENT FOR DE V E LOPMENT 23 
Urbanization continues around the world, 
particularly in developing countries, where rural 
migration continues to fuel urban growth (see 
Figure 1.6). By the end of 2007, more people 
will be living in cities than in rural areas for the 
first time in history (UN-HABITAT 2006). In North 
East Asia and South East Asia, the population 
living in urban areas increased from 28–29 per 
cent in 1985 to 44 per cent in 2005, and is 
projected to reach 59 per cent by 2025 (GEO 
Data Portal, from UNPD 2005). In some places, 
the urban area is increasing faster than the urban 
population, a process known as urban sprawl. 
For example, between 1970 and 1990, the total 
area of the 100 largest urban areas in the United 
States increased by 82 per cent. Only half of 
this increase was caused by population growth 
(Kolankiewicz and Beck 2001) (see Box 1.9). 
A growing number of people living in urban areas 
are living in slums – inadequate housing with no 
or few basic services (UN-HABITAT 2006). In 
many sub-Saharan African cities, children living in 
slums are more likely to die from water-borne and 
respiratory illnesses than rural children. For 2005, 
the number of slum dwellers was estimated at 
almost 1 billion (UN-HABITAT 2006). 
Migration and urbanization have complex relationships 
with environmental change. Natural disasters, and 
degradation of land and local ecosystems are among 
the causes of migration (Matutinovic 2006). Changing 
demographic patterns, caused by migration or 
urbanization, alter land use and demand for ecosystem 
services (see Box 1.9). 
Las Vegas, the fastest growing metropolitan area in the United States, 
exemplifies the problems of rampant urban sprawl. As the gaming 
and tourism industry blossomed, so has the city’s population. In 1985, 
Las Vegas was home to 557 000 people, and was the 66th largest 
metropolitan area in the United States. In 2004, the Las Vegas-Paradise 
area was ranked 32nd in size, with a permanent population nearing 
1.7 million. According to one estimate, it may double by 2015. 
Population growth has put a strain on water supplies. 
Satellite imagery of Las Vegas provides a dramatic illustration of the 
spatial patterns and rates of change resulting from the city’s urban sprawl. 
The city covers the mainly green and grey areas in the centre of these 
images recorded in 1973 and 2000. Note the proliferation of roads 
and other infrastructure (the rectangular pattern of black lines) and the 
dramatic increase in irrigated areas. 
Box 1.9 Urban sprawl, Las Vegas 
Source: UNEP 2005b 
Credit: UNEP 2005b
Figure 1.7 Gross domestic product – purchasing power parity per capita 
thousand US$ 
35 
30 
25 
20 
15 
5 
Urbanization in particular can exert significant 
pressure on the environment (see Chapter 6). 
Coastal urban areas often cause offshore water 
pollution. Coastal populations alone are expected 
to reach 6 billion by 2025 (Kennish 2002). 
In these areas, large-scale development results 
in excessive nutrient inputs from municipal and 
industrial waste. As described in Chapter 4, 
eutrophication contributes to the creation of dead 
zones, areas of water with low or no dissolved 
oxygen. Fish cannot survive, and aquatic 
ecosystems are destroyed. Dead zones are an 
emerging problem in Asia, Africa and South 
America, but are present around the world. With 
Box 1.10 Debt repayments continue to be a major impediment to growth 
24 SECTION A: OVERVIEW 
population growth, and increasing industrialization 
and urbanization, dead zones can only continue to 
expand. Properly managed, cities can also become 
a solution for some of the environmental pressures. 
They provide economies of scale, opportunities for 
sustainable transport and efficient energy options. 
Economic growth 
Global economic growth has been spectacular 
during the last two decades. Gross domestic 
product per capita (at purchasing power parity) 
increased by almost 1.7 per cent annually, but 
this growth was unevenly spread (see Figure 1.7). 
People in Africa, Eastern Europe and Central 
Asia, and certain areas of Latin America and 
the Caribbean are worse off than those in North 
America and Central and Western Europe. Many 
countries in these regions experienced no growth 
and some even a clear economic decline between 
1987 and 2004. Especially in Africa there are 
large differences within the region, and even where 
there is growth, countries are faced with a heavy 
debt burden (see Box 1.10). Income in Asia and 
the Pacific is still well below the global average, 
but its growth rate was twice the global average. 
These sub-regional differences are highlighted in 
Chapter 6. 
Economic growth and unsustainable consumption 
patterns represent a growing pressure on the 
environment, though this pressure is often distributed 
unequally. Dasgupta (2002) argues that economic 
growth is unsustainable in poor countries, partly 
40 
0 
1987 
2004 
Africa Asia and the Pacific Europe Latin America and the Caribbean North America 
Source: GEO Data Portal, 
compiled from World Bank 
2006b 
10 
Even though Africa has only 5 per cent of the developing world’s income, it carries 
about two-thirds of the Global South’s debt burden – over US$300 billion. Despite 
extreme poverty, sub-Saharan Africa transfers US$14.5 billion a year to rich nations 
in external debt repayments. The average sub-Saharan African country, therefore, 
spends three times more on repaying debt than it does on providing basic services to 
its people. By the end of 2004, Africa spent about 70 per cent of its export earnings 
on external debt servicing. At the 2005 Gleneagles Summit, G8 countries cancelled 
100 per cent of debts of a number of eligible Heavily Indebted Poor Countries to 
three multilateral institutions – the International Monetary Fund (IMF), International 
Development Association (IDA) and African Development Fund. This was a step 
towards relieving the burden that debt repayment places on growth and social 
services. As a result of debt cancellation and targeted aid increases between 2000 
and 2004, 20 million more children in Africa are in school. While G8 countries 
reaffirmed Gleneagles commitments at the 2007 Heiligendamm Summit, their ability to 
fulfill these promises has been questioned. 
Sources: Christian Reformed Church 2005, DATA 2007, Katerere and Mohamed-Katerere 2005
ENV I RONMENT FOR DE V E LOPMENT 25 
because it is sustainable in wealthy countries. 
Countries that export resources are subsidizing the 
consumption of importing countries (Dasgupta 2002). 
However, consumption patterns among regions are 
changing with the emergence of new economies 
and powers such as China, India, Brazil, South 
Africa and Mexico. China, for example, is expected 
to become the world’s largest economy between 
2025 and 2035. Its rapid economic development 
is influencing global patterns of resource production 
and consumption, with both environmental and 
geopolitical consequences (Grumbine 2007). Vehicle 
ownership patterns illustrate the impact of changing 
consumption patterns (see Chapter 2). China had 
some 27.5 million passenger vehicles and 79 million 
motorcycles in use by 2004 (CSB 1987–2004). 
The growing trend in vehicle ownership affects 
urban air quality, which has clear consequences 
for human health. 
Globalization 
The world’s economy has been characterized by 
growing globalization, which is spurring the increasing 
integration of the global economy through trade and 
financial flows, and in the integration of knowledge 
through the transfer of information, culture and 
technology (Najam and others 2007). Governance 
has also become globalized, with increasingly 
complex interstate interactions, and with a growing 
role for non-state actors. International companies 
have become influential economic actors in a global 
governance context traditionally dominated by 
nations. While states “rule the world,” corporations 
have publicly sought the global political stage at 
gatherings such as the World Economic Forum and 
at multilateral negotiations, such as the Multilateral 
Agreement on Investment (De Grauwe and Camerman 
2003, Graham 2000). Advances in technology 
and communications, such as the Internet, have also 
boosted the role of individuals and organizations as 
key players in a globalized world (Friedman 2005). 
Globalization raises both fears and expectations. 
Some suggest that increasing interdependence is 
good for cooperation, peace and solving common 
problems (Bhagwati 2004, Birdsall and Lawrence 
1999, Russett and Oneal 2001). Economic 
integration may offer dynamic benefits, such as 
higher productivity. The exchange of goods-and-services 
also helps the exchange of ideas and 
knowledge. A relatively open economy is better 
able to learn and adopt foreign, state-of-the-art 
technologies than is a relatively closed economy 
(Coe and Helpman 1995, Keller 2002). Others, 
however, view growing economic interdependence 
as destabilizing. They say that rapid flows of 
investment into and out of countries cause job 
losses, increase inequality, lower wages (Haass and 
Litan 1998) and result in harm to the environment. 
It is argued that globalization is exploitative, and is 
creating a murkier future for global cooperation and 
justice (Falk 2000, Korten 2001, Mittelman 2000). 
The environment and globalization are intrinsically 
linked. The globalization of trade has facilitated 
the spread of exotic species, including the five 
most important freshwater suspension feeding 
invaders (Dressena polymorpha, D. bugensis, 
Corbicula fluminea, C. fluminalis and Limoperna 
fortunei). The zebra mussel (Dressena polymorpha) 
has spread through North America during the last 
20 years, resulting in significant ecological and 
economic impacts. Its introduction corresponds with 
dramatic increase in wheat shipments between 
the US, Canada and the former Soviet Union 
(Karatayev and others 2007). In a globalized 
world, important decisions related to environmental 
protection may have more to do with corporate 
management and market outcomes than with state-level, 
political factors. Countries may be reluctant 
to enforce strict environmental laws, fearing that 
companies would relocate elsewhere. However, 
it is often forgotten that the environment itself can 
have an impact on globalization. Resources fuel 
global economic growth and trade. Solutions to 
environmental crises, such as climate change, require 
coordinated global action and greater globalization 
of governance (Najam and others 2007). 
Trade 
World trade has continued to grow over the 
past 20 years, as a result of lower transport and 
communication costs, trade liberalization and 
multilateral trade agreements, such as the North 
American Free Trade Agreement. Between 1990 
and 2003, trade in goods increased from 32.5 
to 41.5 per cent of world GDP. Differences exist 
between regions. In North East Asia, trade in 
goods increased from 47 to 70.5 per cent of GDP, 
and high technology exports increased from 16 to 
33 per cent of manufactured exports. By contrast, 
trade in goods in West Asia and Northern Africa
only increased from 46.6 per cent to 50.4 per cent 
of GDP. High technology exports only accounted 
for 2 per cent of manufactured exports in 2002 
(World Bank 2005). Since 1990, least developed 
countries (LDC) have increased their share of world 
merchandise trade, but still accounted for only 
0.6 per cent of world exports and 0.8 per cent of 
world imports in 2004 (WTO 2006). 
As with globalization, a two-way relationship exists 
between the environment and trade. Transport has 
increased as a result of increasing flows of goods and 
global production networks. Transport is now one of 
the most dynamic sectors in a modern economy, and 
has strong environmental impacts (Button and Nijkamp 
2004) (see Chapters 2 and 6). Trade itself can exert 
pressures on the environment. Increases in international 
Source: UNEP 2005b 
26 SECTION A: OVERVIEW 
grain prices may increase the profitability of 
agriculture, and result in the expansion of farming into 
forested areas in Latin America and the Caribbean, 
for example (see Box 1.11). The wildlife trade in 
Mongolia, valued at US$100 million annually, is 
contributing to the rapid decline of species such as 
saiga antelope (World Bank and WCS 2006). In the 
presence of market or intervention failures, international 
trade may also exacerbate environmental problems 
indirectly. For example, production subsidies in the 
fishing sector can promote overfishing (OECD 1994). 
Natural disasters, in turn, can have an impact on 
trade at the national level, when exports fall as a result 
of physical damage. One example of this linkage 
is the hurricane damage to oil refineries in the Gulf 
of Mexico in 2005. Oil production in the Gulf of 
Mexico, which supplies 2 per cent of the world’s crude 
In recent years, Chile has been considered one of the most economically 
competitive countries in Latin America and the Caribbean. Rapid growth in 
Chile’s production and export of forest products is based on the expansion 
and management of exotic species in newly planted forests over the past 
30 years. To do so, the traditional land-use practices in small-scale logging 
of native forests, livestock raising and agricultural cultivation have been 
replaced by large-scale timber production. Many endangered tree and 
shrub species have been affected by this growth of planted forest, which 
has also led to a dramatic reduction of landscape diversity as well as 
goods-and-services from forests. The two images, taken in 1975 (left) and 
2001 (right), show clear reductions in forested land on the one hand (red 
arrows), and new forest areas on the other (yellow arrows). 
Box 1.11 Trade, growth and the environment 
Credit: UNEP 2005b
ENV I RONMENT FOR DE V E LOPMENT 27 
oil, slowed following Hurricane Katrina, and crude oil 
prices jumped to over US$70 a barrel (WTO 2006). 
Trade may also be positive for the environment. 
Debate rages over whether or not free trade will 
raise incomes to a point where environmental 
protection becomes a priority (Gallagher 2004). 
At the 2002 WSSD in Johannesburg, commitments 
were made to expand markets for environmental 
goods-and-services. Liberalization of trade in goods 
that protect the environment may help spur the 
creation of industry dedicated to environmental 
improvements (OECD 2005). Consumer 
preferences can influence production standards, 
which can be used to improve environmental 
conditions. In 2006, a large grain distributor 
imposed a moratorium on the purchase of soy 
produced on deforested areas of the Amazon, 
as a result of a Greenpeace campaign in Europe 
(Cargill 2006, Greenpeace 2006). 
Energy 
The world is facing twin threats: inadequate 
and insecure supplies of energy at affordable 
prices, and environmental damage due to 
overconsumption of energy (IEA 2006a). Global 
demand for energy keeps growing, placing an 
ever-increasing burden on natural resources and 
the environment. For about three decades, world 
primary energy demand grew by 2.1 per cent 
annually, rising from 5 566 million tonnes oil 
equivalent (Mtoe) in 1971 to 11 204 Mtoe in 
2004 (IEA 2006b). Over two-thirds of this increase 
came from developing countries, but OECD 
countries still account for almost 50 per cent of 
world energy demand. In 2004, primary energy 
use per capita in OECD countries was still 10 
times higher than in sub-Saharan Africa. Figure 1.8 
highlights primary energy supply per capita. 
Global increases in carbon dioxide emissions are 
primarily due to fossil fuel use (IPCC 2007), the 
fuels that met 82 per cent of the world’s energy 
demand in 2004. Traditional biomass (firewood 
and dung) remains an important energy source in 
developing countries, where 2.1 billion people rely 
on it for heating and cooking (IEA 2002). Use of 
cleaner energy sources, such as solar and wind 
power, remains minimal overall (see Figure 5.5, 
Chapter 5 for energy supply by source). The need 
to curb growth in energy demand, increase fuel 
kg of oil equivalent per person 
8 000 
7 000 
6 000 
4 000 
3 000 
2 000 
supply diversity and mitigate climate destabilizing 
emissions is more urgent than ever (IEA 2006a). 
However, expansion of alternative energy sources, 
such as biofuels, must also be carefully planned. 
Brazil expects to double the production of ethanol, 
a “modern” biofuel, in the next two decades 
(Government of Brazil 2005). In order to produce 
enough crops to reach production targets, the 
cultivated area is increasing rapidly. The growth 
of farming jeopardizes entire ecoregions, like the 
Cerrado, one of the world’s biodiversity hot spots 
(Klink and Machado 2005). 
Global demand for energy 
keeps growing, placing an ever-increasing 
burden on natural 
resources and the environment. 
Credit: Ngoma Photos 
Figure 1.8 Primary energy supply per capita 
Source: GEO Data Portal, 
from IEA 2006a 
9 000 
0 
1987 
2004 
1989 
1995 
2003 
5 000 
1999 
Africa 
Asia and the Pacific 
Europe 
Latin America and the Caribbean 
North America 
West Asia 
1991 
1993 
1997 
2001 
1 000
Technological innovation 
Advances in agriculture, energy, medicine and 
manufacturing have offered hope for continued 
human development and a cleaner environment. 
New farming technologies and practices related 
to water use, fertilizer and plant breeding have 
transformed agriculture, increasing food production 
and addressing undernutrition and chronic famine 
in some regions. Since 1970, food consumption 
is increasing in all regions, and is expected to 
continue to increase as a result of economic 
development and population growth. Concerns 
have been raised over the ability to meet future 
demand: 11 per cent of the world’s land is already 
used for agriculture, and in many places little room 
exists for agricultural expansion due to land or 
water shortages. Biotechnology, including genetic 
modification, as well as nanotechnology, has the 
potential to increase production in agriculture and 
contribute to advances human health (UNDP 2004), 
but remains subject to much controversy over effects 
on health and the environment. Earlier lessons from 
new technologies show the importance of applying 
the precautionary approach (CIEL 1991), because 
unintended effects of technological advances can 
lead to the degradation of ecosystem services. For 
example, eutrophication of freshwater systems and 
hypoxia in coastal marine ecosystems result from 
excess application of inorganic fertilizers. Advances 
Number of subscribers 
500 
300 
200 
100 
28 SECTION A: OVERVIEW 
in fishing technologies have contributed significantly 
to the depletion of marine fish stocks. 
Communications and cultural patterns have 
also been revolutionized in the last 20 years, 
with the exponential growth of the Internet and 
telecommunications (see Figure 1.9). Worldwide, 
mobile phone subscribers increased from 2 per 
1 000 people in 1990 to 220 per 1 000 in 2003 
and worldwide Internet use increased from 1 in 
1 000 in 1990 to 114 per 1 000 in 2003 (GEO 
Data Portal, from ITU 2005). Many developed 
countries lead the way in the number of Internet 
users, hosts and secure servers, prompting some 
to claim that there is a digital divide between 
different regions of the world. In Australia and 
New Zealand, for example, only 4 per cent of the 
population used Internet in 1996, but by 2003, 
that had risen to 56 per cent of the population 
By contrast in 2003, in poor countries such as 
Bangladesh, Burundi, Ethiopia, Myanmar and 
Tajikistan only 1 or 2 people per 1 000 used the 
Internet (GEO Data Portal, from ITU 2005). 
Governance 
The global and regional political context has 
changed considerably since the Brundtland 
Commission, with the end of the Cold War 
triggering renewed optimism in multilateral and 
Figure 1.9 (a) Mobile phones, per 1 000 people and (b) Internet users, per 100 people, by region 
Source: GEO Data Portal, 
compiled from ITU 2005 
600 
0 
1990 
2003 
1995 
2002 
400 
1999 
Africa 
Asia and the Pacific 
Europe 
Latin America and the Caribbean 
North America 
West Asia 
1991 
1993 
1997 
2001 
a 
1992 
1994 
1996 
1998 
2000 
Number of users 
60 
50 
30 
20 
10 
0 
1990 
2003 
1995 
2002 
40 
1999 
1991 
1993 
1997 
2001 
b 
1992 
1994 
1996 
1998 
2000
ENV I RONMENT FOR DE V E LOPMENT 29 
global governance. The 1990s was a decade of 
global summits on a diversity of issues, including 
children (1990), sustainable development (1992), 
human rights (1994), population (1994), social 
development (1995), gender equality (1995) and 
human settlements (1996). The new millennium 
has been equally active and agenda-setting, 
starting with the Millennium Summit in 2000, and 
its follow-up in 2005. Normative declarations 
and ambitious action plans from all these summits 
illustrate an emerging unity in how governments and 
the international community understand complex 
and global problems and formulate appropriate 
responses. The establishment of the World Trade 
Organization in 1994 strengthened global 
governance through its considerable authority in 
the areas of trade, while the establishment of the 
International Criminal Court of Justice in 2002 
attempted to do the same for crimes against 
humanity. Some important reforms have happened 
within the UN system, including an approach that 
increasingly uses partnerships (such as the Global 
Water Partnership) and institutionalized processes to 
strengthen the participation of civil society (such as 
the UNEP’s Global Civil Society Forum and Global 
Women’s Assembly on Environment). 
At the regional level, countries have expanded or 
established institutions to enhance cooperation, 
including the European Union (EU), the North 
American Free Trade Agreement (NAFTA), the Southern 
Common Market (MERCOSUR), the Association of 
Southeast Asian Nations (ASEAN) and the African 
Union (AU). Regions became more visible in global 
deliberations, through, for example, the emphasis on 
regional preparation meetings for the World Summit on 
Sustainable Development. 
The national level remains central in governance, 
despite discussions in the context of globalization 
and regionalization. Some countries are adopting 
innovative governance systems and there has 
been a trend towards both political and fiscal 
decentralization of governance to sub-national 
levels. This does not necessarily mean that local 
authorities have been empowered. It has been 
argued that decentralization without devolution of 
power can be a way to strengthen the presence 
of the central authority (Stohr 2001). Local 
governments have also engaged much more widely 
in international cooperation in various arenas, 
and their role has been strengthened at the global 
level through the establishment in 2000 of the UN 
Advisory Committee of Local Authorities (UNACLA) 
and the World Urban Forum in 2002, as well 
as the founding of the United Cities and Local 
Governments Organization in 2004. 
RESPONSES 
Interactions between drivers and pressures, and 
their consequent impacts on ecosystem services 
and human well-being present challenges that 
could not be foreseen in 1987. There is an urgent 
need for effective policy responses at all levels 
– international, regional, national and local. As 
highlighted in the other chapters of this report, the 
range and scope of response options available 
to policy-makers has progressively evolved over 
the past 20 years (see Box 1.12), with a diversity 
of multilateral environmental agreements and 
institutions now involved in trying to address the 
challenges. The increase in governance regimes 
has brought about its own challenges, including 
competition and overlap. An interlinkages approach 
is essential to managing the environment, not in its 
individual parts but more holistically. This approach 
recognizes that the environment itself is interlinked; 
land, water and atmosphere are connected in many 
ways, particularly through the carbon, nitrogen 
and water cycles. Chapter 8 highlights both the 
biophysical and governance regimes interlinkages. 
Chapter 10 highlights the evolution of policy 
response measures – from a focus on command-and- 
Box 1.12 Types of responses 
Command-and-control regulation includes standards, bans, permits and quotas, 
zoning, liability systems, legal redress, and flexible regulation. 
Direct provisions by government deal with environmental infrastructure, eco-industrial 
zones or parks, protected areas and recreation facilities, and ecosystem rehabilitation. 
Public and private sector engagement relates to public participation, decentralization, 
information disclosure, eco-labelling, voluntary agreements and public-private 
partnerships. 
Market use includes environmental taxes and charges, user charges, deposit-refund 
systems, targeted subsidies, and the removal of perverse subsidies. 
Market creation addresses issues of property rights, tradeable permits and rights, 
offset programmes, green programmes, environmental investment funds, seed funds and 
incentives.
control policies to creating markets and incentives, 
particularly for industry to implement voluntary 
measures aimed at minimizing environmental 
damage. For conventional, well-known 
environmental problems with proven solutions, it 
is necessary to continue to apply, and to further 
improve upon previously successful approaches. 
Countries that have yet to address such problems 
should apply these proven, workable solutions to 
current problems. Previously successful approaches 
have generally addressed changes to pressures, for 
example by regulating emission levels, land use or 
resource extraction. In order to address less-known 
persistent (or emerging) problems, transformative 
policies are needed. These policies address 
the drivers of environmental problems, such as 
demographic change and consumption patterns. 
Adaptive management is essential, to enable policy-makers 
30 SECTION A: OVERVIEW 
to learn from previous experience as well 
as to make use of a variety of new tools that may 
be needed. 
Economic instruments 
Today, greater emphasis is being placed on the 
potential use of economic instruments to help 
correct market failures. These instruments were 
promoted by Principle 16 of the Rio Declaration: 
“National authorities should endeavour to promote 
the internalization of environmental costs and the 
use of economic instruments.” 
Natural resources can be seen as a capital 
asset belonging to a general portfolio, which 
is comprised of other assets and capitals, 
including material, financial, human and social. 
Managing this portfolio in a good and sustainable 
manner to maximize its returns and benefits over 
time is good investment. It is also central to 
sustainable development. 
A variety of economic instruments exist, including 
property rights, market creation, fiscal instruments, 
charge systems, financial instruments, liability 
systems, and bonds and deposits. There is a mix 
of so-called market-based instruments (MBIs) and 
command-and-control instruments to enable policy-makers 
to better manage and get more accurate 
information regarding the portfolio of capital 
assets. Table 1.2 summarizes different economic 
instruments, and how they can be applied to 
different environmental sectors. One of the tools is 
valuation, which can be used to help better assess 
the value of ecosystem services, and the costs of 
human-induced changes to the environment. 
Valuation 
Environmental ministries and agencies are often the 
last to benefit from investments, because economics 
and growth generation take precedence in government 
spending decisions. This is often due to lack of 
information on the value and carrying limits of the 
Earth’s ecosystems. Measurement of economic 
development and progress has often been linked to 
measures of economic output such as Gross National 
Product (GNP). Such aggregate measurements do not 
consider the depletion of natural capital caused by the 
consumption and production of goods-and-services. 
National accounting systems need revision to better 
include the value of the changes in the environmental 
resource base due to human activities (Mäler 1974, 
Dasgupta and Mäler 1999). 
Valuing different goods-and-services involves 
comparisons across different sets of things. How 
these things are accounted for, and how the 
services provided by the ecosystems, for example, 
improve well-being is called the accounting 
price. Table 1.3 illustrates different approaches 
to valuation, and how these approaches might 
be used to help assess the impact of policies on 
environmental change and human well-being. 
A “set of institutions capable of managing the 
natural resources, legal frameworks, collecting 
resource rents, redirecting these rents into profitable 
investments” is key to effective use of valuation 
(World Bank 2006a). Valuing natural resources 
and evaluating policies where institutions such as 
markets do not exist, and where there is a lack 
of individual property rights, pose challenges. 
Under such uncertainties, and where divergent sets 
of values exist, the economic value of common 
resources can be measured by the maximum 
amount of other goods-and-services that individuals 
are willing to give up to obtain a given good 
or service. Therefore, it is possible to weigh the 
benefits from an activity such as the construction 
of a dam against its negative impacts on fishing, 
livelihoods of nearby communities, and changes 
to scenic and aesthetic values. Box 1.13 provides 
an example of non-market valuation using the 
contingent valuation method (CVM).
ENV I RONMENT FOR DE V E LOPMENT 31 
Table 1.2 Economic instruments and applications 
Property rights Market creation 
Fiscal 
instruments Charge systems 
Financial 
instruments 
Liability 
systems 
Bonds and 
deposits 
Forests Communal 
rights 
Concession 
building 
Taxes and 
royalties 
Reforestation 
incentives 
Natural 
resource 
liability 
Reforestation 
bonds, forest 
management 
bonds 
Water 
resources 
Water rights Water shares Capital gains tax Water pricing 
Water protection 
charges 
Oceans and 
seas 
Fishing rights, 
Individual 
transferable quotas 
Licensing 
Oil spill bonds 
Minerals Mining rights Taxes and 
royalties 
Land 
reclamation 
bonds 
Wildlife Access fees Natural 
resource 
liability 
Biodiversity Patents 
Prospecting 
rights 
Transferable 
development rights 
Charges for scientific 
tourism 
Natural 
resource 
liability 
Water 
pollution 
Tradeable effluent 
permits 
Effluent charges Water treatment fees Low-interest 
loans 
Land and soils Land rights, use 
rights 
Property taxes, 
land-use taxes 
Soil 
conservation 
incentives (such 
as loans) 
Land 
reclamation 
bonds 
Air pollution Tradeable emission 
permits 
Emission charges Technology subsidies, 
low-interest loans 
Hazardous 
waste 
Collection charges Deposit refund 
systems 
Solid waste Property taxes Technology subsidies, 
low-interest loans 
Toxic 
chemicals 
Differential 
taxation 
Legal liability, 
liability 
insurance 
Deposit refund 
Climate Tradeable 
emission 
entitlements 
Tradeable 
forest 
protection 
obligations 
Tradeable CO2 
permits 
Tradeable CFC 
quotas 
CFC quota auction 
Carbon offsets 
Carbon taxes 
BTU tax 
CFC 
replacement 
incentives 
Forest compacts 
Human 
settlements 
Land rights Access fees 
Tradeable 
development quotas 
Transferable 
development rights 
Property taxes, 
land-use taxes 
Betterment charges 
Development charges 
Land-use charges 
Road tolls 
Import fees 
Development 
completion 
bonds 
Source: Adapted from Panayotou 1994
Valuation presents a set of challenges beyond 
conflicting value systems or lack of existing market 
institutions. It uses notional and proxy measures 
to estimate the economic values of tangible and 
intangible services provided by the environment. 
An increasing body of valuation work has been 
undertaken on provisioning services of ecosystems. 
It has produced estimates of the value of non-timber 
forest products, forestry, and the health impacts of 
air pollution and water-borne diseases. However, 
studies on less tangible but yet important services, 
such as water purification and the prevention of 
natural disasters, as well as recreational, aesthetic 
and cultural services, have been hard to get. To get 
objective monetary estimates of these services remains 
a challenge. Market data is limited to a small number 
32 SECTION A: OVERVIEW 
of services provided by ecosystems. Furthermore, 
methodologies such as cost-benefit analysis and CVM 
may raise problems of bias. 
The use of market and non-market-based instruments 
has also shown gaps in addressing distributional and 
intergenerational equity issues (MA 2005b), notably 
with regard to poverty-related issues. Finally, many 
valuation studies estimating the impact of policies 
or projects on human well-being fail due to the lack 
of sufficiently precise estimates of the consequences 
of these policies or projects now and in the future. 
Despite these flaws, valuation may be a useful tool 
with which to examine the complex relationships and 
feedback involving the environment, economic growth 
and human well-being. 
Table 1.3 Purpose and application of different valuation approaches 
Approach Why it is done How it is done 
Determining the total value of 
the current flow of benefits from 
an ecosystem. 
To understand the contribution that 
ecosystems make to society and 
to human well-being. 
Identify all mutually compatible services provided. 
Measure the quantity of each service provided, and multiply by the value of each service. 
Determining the net benefits 
of an intervention that alters 
ecosystem conditions. 
To assess whether the intervention 
is worthwhile. 
Measure how the quantity of each service would change as a result of the intervention, 
as compared to their quantity without the intervention. 
Multiply by the marginal value of each service. 
Examining how the costs and 
benefits of an ecosystem (or an 
intervention) are distributed. 
To identify winners and losers, for 
ethical and practical reasons. 
Identify relevant stakeholder groups. 
Determine which specific services they use, and the value of those services to that group 
(or changes in values resulting from an intervention). 
Identifying potential financing 
sources for conservation. 
To help make ecosystem 
conservation financially self-sustaining. 
Identify groups that receive large benefit flows from which funds could be extracted, using 
various mechanisms. 
Source: Adapted from Stephano 2004 
An environmental impact analysis using CVM was conducted in 
the 1990s to explore the removal of the Elwha and Glines dams in 
Washington State in the United States. These two 30- and 60-metre-high 
dams, respectively, are old, and block the migration of fish to 110 km of 
pristine water located in the Olympic National Park. The dams also harm 
the Lower Elwha Klallam Tribe which relies on the salmon and river for 
their physical, spiritual and cultural well-being. Dam removal could bring 
substantial fishing benefits, more than tripling the salmon populations. 
The cost of removing the dams, and especially the sediment build-up is 
estimated at about US$100–$125 million. Recreational and commercial 
fishing benefits resulting from dam removal would not be sufficient to 
cover these costs. 
A CVM survey was conducted and yielded a 68 per cent response in 
Washington State, and 55 per cent response for the rest of the United 
States. Willingness to pay for dam removal ranged from US$73 per 
household for Washington to US$68 for the rest of the United States. 
If every household in Washington State were to pay US$73, the cost 
of dam removal and river restoration could be covered. If the return 
stemming from Washington residents’ willingness to pay was added to 
the rest of the US willingness to pay (the 86 million households and their 
willingness to pay an average of US$68 per head) in excess of US$1 
billion dollars would result. 
After years of negotiations it has been decided that the dams will be 
removed, and the Elwha Restoration Project will go forward. This is 
the biggest dam-removal project in history, and an event of national 
significance in the United States. It is expected that the two dams will 
be removed in stages over the course of three years, between 2009 
and 2011. 
Box 1.13 Valuing the removal of the Elwha and Glines Dams 
Source: American Rivers 2006, Loomis 1997, USGS 2006
Box 1.14 The UN Decade of Education for Sustainable 
Development 
ENV I RONMENT FOR DE V E LOPMENT 33 
Non-economic instruments 
In addition to economic instruments, a variety of non-economic 
instruments have been employed to address 
both well-known proven and less clear emerging 
(or persistent) environmental problems. Today, 
the emerging understanding of human well-being 
increasingly influences our choice of instruments. 
Public participation 
Human well-being depends on the unconstrained 
ability of people to participate in decisions, so 
that they can organize society in a way that is 
consistent with their highest values and aspirations. 
In other words, public participation is not only a 
matter of procedural justice, but also a precondition 
for achieving well-being. While this is challenging, 
managers should involve civil society in policy 
interventions. The Convention on Biological Diversity 
offers several examples of possible stakeholder 
engagement in decision making. These include 
CBD VII/12, The Addis Ababa Guidelines on the 
sustainable use of the components of biodiversity; 
CBD VII/14 guidelines on sustainable tourism 
development; and the CBD VII/16 Akwe, on 
voluntary guidelines for the conduct of cultural, 
environmental and social impact assessments for 
development proposals on sacred sites, lands 
and waters traditionally occupied or used by 
indigenous and local communities. The development 
of similar agreements and protocols that enhance 
effective engagement of all sectors of society 
should be encouraged. 
Education 
Access to information and education is a basic 
human right, and an important aspect of human 
well-being. It is also an important tool for 
generating knowledge that links ecological analyses 
to societal challenges, and is critical to the decision 
making process. Women and marginalized 
communities must be ensured access to education. 
The United Nations launched its Decade of 
Education for Sustainable Development (DESD) in 
2005 and designated UNESCO as lead agency 
for the promotion of the Decade (see Box 1.14). 
Justice and ethics 
Since the environment affects the very basis of human 
well-being, it is a matter of justice to consider the 
impacts of environmental degradation on others, and 
attempt to minimize harm for both current and future 
generations. It has been argued that a “global ethic” 
is required to address the problems of the 21st century 
(Singer 2002). The intrinsic value of species has also 
been recognized (IUCN and others 1991). The pursuit 
of some people’s opportunities and freedoms may 
harm or limit those of others. It is important that policy-makers 
consider the adverse effects their decisions 
have on people and the environment in other areas or 
regions, since such communities do not participate in 
local decision making. 
Scenario development 
The use of scenarios to inform policy processes is 
growing, providing policy-makers with opportunities 
to explore the likely impacts and outcomes of various 
policy decisions. The goal of developing scenarios “is 
often to support more informed and rational decision 
making that takes both the known and unknown into 
account” (MA 2005c). Their purpose is to widen 
perspectives and illuminate key issues that might 
The overall goal of the DESD is “to integrate the 
principles, values, and practices of sustainable 
development into all aspects of education and 
learning.” 
This educational effort will encourage changes in 
behaviour that will create a more sustainable future 
in terms of environmental integrity, economic viability, 
and a just society for present and future generations. 
In the long-term, education must contribute to 
government capacity building, so that scientific 
expertise can inform policy. 
Source: UNESCO 2007
otherwise be missed or dismissed. Chapter 9 uses four 
plausible scenarios to explore the impact of different 
policy decisions on environmental change and future 
human well-being. 
CONCLUSION 
Two decades after Our Common Future emphasized 
the urgency of sustainable development, environmental 
degradation continues to threaten human well-being, 
endangering health, physical security, social cohesion 
and the ability to meet material needs. Analyses 
throughout GEO-4 also highlight rapidly disappearing 
forests, deteriorating landscapes, polluted waters and 
urban sprawl. The objective is not to present a dark 
and gloomy scenario, but an urgent call for action. 
While progress towards sustainable development 
has been made through meetings, agreements and 
changes in environmental governance, real change 
has been slow. Since 1987, changes to drivers, 
such as population growth, consumption patterns 
and energy use, have placed increasing pressure on 
the state of the environment. To effectively address 
environmental problems, policy-makers should design 
policies that tackle both pressures and the drivers 
behind them. Economic instruments such as market 
creation and charge systems may be used to help spur 
environmentally sustainable behaviour. Valuation can 
help policy-makers make informed decisions about 
the value of changes to ecosystem services. Non-economic 
34 SECTION A: OVERVIEW 
instruments should be used to address both 
well-known problems with proven solutions and less 
clear emerging problems. This chapter has provided 
an overview of the challenges of the 21st century, 
highlighted conceptual ideas that have emerged to 
analyse and understand these environmental problems, 
and indicated options on the way forward. 
The following chapters highlight areas where society 
has contributed to environmental degradation and 
human vulnerability. Everyone depends on the 
environment. It is the foundation of all development, 
and provides opportunities for people and society as a 
whole to achieve their hopes and aspirations. Current 
environmental degradation undermines natural assets, 
and negatively affects human well-being. It is clear 
that a deteriorating environment is an injustice to both 
current and future generations. 
The chapters also emphasize that alternative development 
paths that protect the environment are available. Human 
ingenuity, resilience and capacity to adapt are powerful 
forces from which to draw to effect change. 
Imagine a world in which human well-being for all is 
secure. Every individual has access to clean air and 
water, ensuring improvements in global health. Global 
warming has been addressed, through reductions 
in energy use, and investment in clean technology. 
Assistance is offered to vulnerable communities. 
Species flourish as ecosystem integrity is assured. 
Transforming these images into reality is possible, and 
it is this generation’s responsibility to start doing so. 
Imagine a world in which 
human well-being for all is 
secure. Transforming this into 
reality is possible, and it is this 
generation’s responsibility to start 
doing so. 
Credit: T. Mohr/Still Pictures
ENV I RONMENT FOR DE V E LOPMENT 35 
References 
Agarwal, B. (2000). Conceptualizing Environmental Collective Action: Why Gender 
Matters. In Cambridge Journal of Economics 24(3):283-310 
AMAP (2002). Persistent Organic Polluatants, Heavy Metals, Radioactivity, Human 
Health, Changing Pathways. Arctic monitoring and Assessment Programme, Oslo 
American Rivers (2006). Elwha River Restoration. http://www.americanrivers.org/ 
site/PageServer?pagename=AMR_elwharestoration (last accessed 12 June 2007) 
Bass, S. (2006). Making poverty reduction irreversible: development implications of 
the Millennium Ecosystem Assessment. IIED Environment for the MDGs’ Briefing Paper. 
International Institute on Environment and Development, London 
Bell, D., Robertson, S. and Hunter, P. (2004). Animal origins of SARS coronavirus: 
possible links with the international trade of small carnivores. In Philosophical 
Transactions of the Royal Society London 359:1107-1114 
Bhagwati, J. (2004). In Defense of Globalization. Oxford University Press, Oxford 
Birdsall, N. and Lawrence, R. (1999). Deep Integration and Trade Agreements: Good 
for Developing Countries? In Grunberg, K. and Stern, M (eds.). In Global Public Goods: 
International Cooperation in the 21st Century. Oxford University Press, New York, NY 
Braidotti, R., Charkiewicz, E., Hausler, S. and Wieringa, S. (1994). Women, the 
Environment and Sustainable Development. Zed, London 
Brown, D. (1999). Making CSD Work. In Earth Negotiations Bulletin 3(2):2-6 
Brown, S. (2006). The west develops a taste for bushmeat. In New Scientist 2559:8 
Button, K. and Nijkamp, P. (2004). Introduction: Challenges in conducting transatlantic 
work on sustainable transport and the STELLA/STAR Initiative. In Transport Reviews 
24 (6):635-643 
Campbell, B., Jeffrey, S., Kozanayi, W., Luckert, M., Mutamba, M. and Zindi, C. 
(2002). Household livelihoods in semi-arid regions: options and constraints. Center for 
International Forestry Research, Bogor 
Castles, S. (2002). Environmental change and forced migration: making sense of the 
debate. New Issues in Refugee Research, Working Paper No. 70. United Nations High 
Commission for Refugees, Geneva 
Cargill (2006). Brazilian Soy Industry Announces Initiative Designed To Curb 
Soy-Related Deforestation in the Amazon. http://www.cargill.com/news/issues/ 
issues_soyannouncement_en.htm (last accessed 11 June 2007) 
Carothers, T. and Barndt, W. (2000). Civil Society. In Foreign Policy (11):18-29 
China Statistical Bureau (1987-2004). China Statistical Yearbook (1987-2004). China 
28 Statistics Press (in Chinese), Beijing 
CIEL (1991). The Precautionary Principle: A Policy for Action in the Face of Uncertainty. 
King’s College, London 
Cleaver, F. (2000). Analysing Gender Roles in Community Natural Resource 
Management: Negotiation, Life Courses, and Social Inclusion. In IDS Bulletin 
31(2):60-67 
Coe, D. T. and Helpman, E. (1995). International R&D Spillovers. NBER Working 
Papers 4444. National Bureau of Economic Research, Inc, Cambridge, MA 
Christian Reformed Church (2005). Global Debt. An OSJHA Fact Sheet. Office of Social 
Justice and Hunger Action http://www.crcna.org/site_uploads/uploads/factsheet_ 
globaldebt.doc (last accessed 21 April 2007) 
CHS (2006). Outline of the Report of the Commission on Human Security. Commission 
on Human Security http://www.humansecurity-chs.org/finalreport/Outlines/outline. 
pdf (last accessed 1 May 2007) 
Conca, K. and Dabelko, G. (2002). Environmental Peacemaking. Woodrow Wilson 
Center Press, Washington, DC 
Dabelko, D., Lonergan, S. and Matthew, R. (2000). State of the Art Review of 
Environmental Security and Co-operation. Organisation for Economic Cooperation and 
Development, Paris 
Dasgupta, P. (2002). Is contemporary economic development sustainable? In Ambio 
31(4):269-271 
Dasgupta, P. and Mäler, K.G. (1999). Net National Product, Wealth, and Social Well- 
Being. In Environment and Development Economics 5:69-93 
DATA (2007). The DATA Report 2007: Keep the G8 Promise to Africa. Debt AIDS Trade 
Africa, London 
De Grauwe, P. and Camerman, F. (2003). Are Multinationals Really Bigger Than 
Nations? In World Economics 4 (2):23-37 
Delgado, C., Wada, N., Rosegrant, M., Meijer, S. and Ahmed, M. (2003). Outlook for 
fish to 2020. In Meeting Global Demand. A 2020 Vision for Food, Agriculture, and the 
Environment Initiative, International Food Policy Research Institute, Washington, DC 
Dernbach, J. (2002). Stumbling Toward Sustainability. Environmental Law Institute, 
Washington, DC 
DeSombre, E.R. and Barkin, S. (2002). Turbot and Tempers in the North Atlantic. 
In Matthew, R. Halle, M. and Switzer, J (eds.). In Conserving the Peace: Resources, 
Livelihoods, and Security 325-360. International Institute for Sustainable Development 
and The World Conservation Union, Winnipeg, MB 
Diamond, J. (2005). Collapse: How Societies Choose to Fail or Survive. Penguin 
Books, London 
Diener, E. (2000). Subjective well-being. The science of happiness and a proposal for a 
national index. In The American Psychologist 55:34-43 
Dodds, F. and Pippard, T. (eds.) (2005). Human and Environmental Security: An 
agenda for change. Earthscan, London 
Donaldson, S. (2002). Re-thinking the mercury contamination issue in Arctic Canada. 
M.A. Thesis (Unpublished). Carleton University, Ottawa, ON 
Doubleday, N. (1996). “Commons” concerns in search of uncommon solutions: 
Arctic contaminants, catalyst of change? In The Science of the Total Environment 
186:169-179 
Doubleday, N. (2005). Sustaining Arctic visions, values and ecosystems: writing Inuit 
identity, reading Inuit Art. In Williams, M. and Humphrys, G. (eds.). Cape Dorset, 
Nunavut’ in Presenting and Representing Environments: Cross-Cultural and Cross- 
Disciplinary Perspectives. Springer, Dordrecht 
EM-DAT (undated). Emergency Events Database: The OFDA/CRED International Disaster 
Database (in GEO Data Portal). Université Catholique de Louvain, Brussels 
Fa, J., Albrechtsen, L. and Brown. D. (2007). Bushmeat: the challenge of balancing 
human and wildlife needs in African moist tropical forests. In Macdonald, D. and 
Service, K. (eds.) Key Topics in Conservation Biology 206-221. Blackwell Publishing, 
Oxford 
Falk, R. (2000). Human rights horizons: the pursuit of justice in a globalizing world. 
Routledge, New York, NY 
FAO (2004a). The State of Food and Agriculture 2003-2004: Agriculture 
Biotechnology-Meeting the Needs of the Poor? Food and Agriculture Organization of the 
United Nations, Rome http://www.fao.org/WAICENT/FAOINFO/ECONOMIC/ESA/en/ 
pubs_sofa.htm (last accessed 11 June 2007) 
FAO (2004b). The State of the World’s Fisheries and Aquaculture 2004. Food and 
Agriculture Organization of the United Nations, Rome 
Fischetti, M. (2005). Protecting against the next Katrina: Wetlands mitigate flooding, 
but are they too damaged in the gulf? In Scientific American October 24 
Frey, B and Stutzer, A. (2005). Beyond Outcomes: Measuring Procedual Utility. In 
Oxford Economic Papers 57(1):90-111 
Friedman, T. (2005). The World is Flat: A Brief History of the Twenty-First Century. 
Farrar, Straus, and Giroux, New York, NY 
Gallagher, K. (2004). Free Trade and the Environment: Mexico, NAFTA and Beyond. 
Stanford University Press, Stanford 
GEF (2006). What is the GEF? The Global Environment Facility, Washington, DC 
http://www.gefweb.org/What_is_the_GEF/what_is_the_gef.html (last accessed 
1 May 2007) 
GEO Data Portal. UNEP’s online core database with national, sub-regional, regional 
and global statistics and maps, covering environmental and socio-economic data and 
indicators. United Nations Environment Programme, Geneva http://www.unep.org/ 
geo/data or http://geodata.grid.unep.ch (last accessed 12 June 2007) 
Goodall, J. (2005). Introduction. In Reynolds, V. (ed.). The Chimpanzees of the 
Budongo Forest. Oxford University Press, Oxford 
Gore, A. (2006). An Inconvenient Truth: the planetary emergency of global warming 
and what we can do about it. Bloomsbury, London 
Graham, E. (2000). Fighting the Wrong Enemy: Antiglobal Activists and Multinational 
Enterprises. Institute of International Economics, Washington, DC 
Greenpeace (2006). The future of the Amazon hangs in the balance. http://www. 
greenpeace.org/usa/news/mcvictory (last accessed 11 June 2007) 
Grumbine, R. (2007). China’s emergence and the prospects for global sustainability. In 
BioScience 57 (3):249-255 
Haass, R., and Litan, R. (1998). Globalization and Its Discontents: Navigating the 
Dangers of a Tangled World. In Foreign Affairs 77(3):2-6 
Hecker, J.H. (2005). Promoting Environmental Security and Poverty Alleviation in the 
Peat Swamps of Central Kalimantan, Indonesia. Institute of Environmental Security, 
The Hague 
IEA (2002). World Energy Outlook 2003. International Energy Agency, Paris 
IEA (2006a). World Energy Outlook 2006. International Energy Agency, Paris 
IEA (2006b). Key Energy Statistics. International Energy Agency, Paris 
IFAD (2001). Rural Poverty Report 2001. The Challenge of Ending Rural Poverty. 
International Fund for Agricultural Development, Rome http://www.ifad.org/poverty/ 
index.htm (last accessed 1 May 2007) 
IFPRI (2004). Ending Hunger in Africa: Prospects for the Small Farmer. International 
Food Policy Research Institute, Washington, DC http://www.ifpri.org/pubs/ib/ib16. 
pdf (last accessed 1 May 2007) 
IPCC (2001). Technical Summary, Climate Change 2001: Impacts, Adaptation and 
Vulnerability. Contribution of Working Group II to the Third Assessment Report of the 
Intergovernmental Panel on Climate Change. Intergovernmental Panel on Climate 
Change. Cambridge University Press, New York, NY 
IPCC (2007). Climate change 2007: The Physical Science Basis. Summary for 
Policymakers. Contribution of Working Group 1 to the Fourth Assessment Report of the 
Intergovernmental Panel on Climate Change, Geneva 
ITU (2005). ITU Yearbook of Statistics. International Telecommunication Union (in 
GEO Data Portal). 
IUCN, UNEP and WWF (1991). Caring for the Earth: A Strategy for Sustainable Living. 
The World Conservation Union, United Nations Environment Programme and World 
Wide Fund for Nature, Gland 
Jänicke, M. and Volkery, A. (2001). Persistente Probleme des Umweltschutzes. In 
Natur und Kultur 2(2001):45-59 
Karatayev, A., Padilla, D., Minchin, D., Boltovskoy, D. and Burlakova, L. (2007). 
Changes in global economies and trade: the potential spread of exotic freshwater 
bivalves. In Bio Invasions 9:161-180 
Karesh, W., Cook, R., Bennett, E. and Newcomb, J. (2005). Wildlife Trade and Global 
Disease Emergence. In Emerging Infectious Diseases 11 (7):1000-1002 
Katerere, Y. and Hill, R. (2002). Colonialism and inequality in Zimbabwe. In Matthew, 
R., Halle, M. and Switzer, J. (eds.). Conserving the Peace: Resources, Livelihoods, and 
Security 247-71 International Institute for Sustainable Development and The World 
Conservation Union, Winnipeg and Gland 
Katerere, Y. and Mohamed-Katerere, J. (2005). From Poverty to Prosperity: Harnessing 
the Wealth of Africa’s Forests. In Mery, G., Alfaro, R., Kanninen, M. and Lobovikov, M. 
(eds.). Forests in the Global Balance – Changing Paradigms. IUFRO World Series Vol. 
17. International Union of Forest Research Organizations, Helsinki 
Keller, W. (2002). Trade and the Transmission of Technology. In Journal of Economic 
Growth 7:5-24 
Kennish, M. (2002). Environmental Threats and Environmental Future of Estuaries. In 
Environmental Conservation 29 (1):78 – 107 
Kerr J., Pangare G., and Pangare V. (2002). Watershed development projects in India: 
An evaluation. In Research Report of the International Food Policy Research Institute 
127:1-90 
Klink, C. and Machado, R. (2005). Conservation of the Brazilian Cerrado. In 
Conservation Biology 19 (3):707-713 
Kolankiewicz, L. and Beck, R. (2001). Weighing Sprawl Factors in Large U.S. Cities, 
Analysis of U.S. Bureau of the Census Data on the 100 Largest Urbanized Areas of the 
United States. http://www.sprawlcity.org (last accessed 1 May 2007) 
Korten, D. (2001). When Corporations Rule the World, 2nd edition. Kumarian Press, 
Bloomfield 
Kura,Y., Revenga, C., Hoshino, E. and Mock, G. (2004). Fishing for Answers: Making 
Sense of the Global Fish Crisis. World Resources Institute, Washington, DC 
Langhelle, O. (1999). Sustainable development: exploring the ethics of Our Common 
Future. In International Political Science Review 20 (2):129-149 
Le Billion, P. (2001). The political Ecology of war: natural resources and armed conflict. 
In Political Geography 20:561-584 
LeRoy, E., Rouquet, P., Formenty, P., Souquière, S., Kilbourne, A., Froment, J., 
Bermejo, M., Smit, S., Karesh, W., Swanepoel, R., Zaki, S. and Rollin, P. (2004). 
Multiple Ebola virus transmission events and rapid decline of central African wildlife. In 
Science 303:387-390 
Li, W., Shi, Z., Yu, M., Ren, W., Smith, C., Epstein, J. Wang, H. Crameri, G., Hu., Z., 
Zhang, H., Zhang, J., McEachern, J., Field, H., Daszak, P., Eaton, B., Zhang, S. and 
Wang, L. (2005). Bats are natural reservoirs of SARS-like coronavirsues. In Science 
310:676-679 
Loomis, J. (1997). Use of Non-Market Valuations Studies. Water Resources 
Management Assessments. In Water Resources Update 109:5-9 
MA (2003). Ecosystems and Human Well-being; a framework for assessment. 
Millennium Ecosystem Assessment. Island Press, Washington, DC 
MA (2005a). Ecosystems and Human well-being: Biodiversity Synthesis. Millennium 
Ecosystem Assessment. World Resources Institute. Island Press, Washington, DC
MA (2005b). Ecosystems and Human Well-Being. Synthesis Report. Millennium 
Ecosystem Assessment. Island Press, Washington, DC 
MA (2005c). Ecosystems and Human Well-being: Volume 2 – Scenarios. Millennium 
Ecosystem Assessment. Island Press, Washington, DC 
MacDonald, D. and Service, K (2007). Key Topics in Conservation Biology. Blackwell 
Publications, Oxford 
Mäler, K-G. (1974). Environmental Economics: A Theoretical Enquiry. John Hopkins 
University Press, Baltimore, MB 
Maltais, A., Dow, K. and Persson, A. (2003). Integrating Perspectives on Environmental 
Security. SEI Risk and Vulnerability Programme, Report 2003-1. Stockholm 
Environment Institute, Stockholm 
Matthews, D. (1995). Common versus open access. The collapse of Canada’s east 
coast fishery. In The Ecologist 25:86-96 
Matthew, R., Halle, M. and Switzer, J. (eds.) (2002). Conserving the Peace: 
Resources, Livelihoods and Security. International Institute for Sustainable Development, 
Winnipeg, MB 
Matutinovic, I. (2006). Mass migrations, income inequality and ecosystem health in 
the second wave of globalization. In Ecological Economics 59:199 – 203 
McMichael, A. (2001). Human culture, ecological change and infectious disease: are 
we experiencing history’s fourth great transition? In Ecosystem Health (7):107-115 
McMichael, A. (2004). Environmental and social influences on emerging infectious 
disease: past, present and future. Philosophical Transactions of the Royal Society of 
London Biology 10:1-10 
Meredith, M. (2005).The State of Africa: A history of fifty years of independence. 
Free Press, London 
Government of Brazil (2005). Diretrizes de Política de Agroenergia 2006–2011. 
Ministério da Agricultura, Pecuária e Abastecimento, Ministério da Ciência e Tecnologia, 
Ministério de Minas e Energia, Ministério do Desenvolvimento, Indústria e Comércio 
Exterior, Brasilia 
Mittelman, J. (2000). Capturing Globalization. Carfax, Abingdon 
Myers, N. (1997). Environmental Refugees. In Population and Environment 
19(2):167-82 
Najam, A., Runnalls, D. and Halle, M. (2007). Environment and Globalization: Five 
Propositions. International Institute for Sustainable Development, Winnipeg 
Nishikiori, N., Abe, T., Costa, D., Dharmaratne, S., Kunii, O. and Moji, K. (2006). Who 
died as a result of the tsunami? Risk factors of mortality among internally displaced 
persons in Sri Lanka: a retrospective cohort analysis. In BMC Public Health 6:73 
OECD (2005). Trade that Benefits the Environment and Development: Opening Markets 
for Environmental Goods and Services. Organisation for Economic Co-operation and 
Development, Paris 
OECD (1994). The Environmental Effects of Trade. Organisation for Economic Co-operation 
and Development, Paris 
Oxfam (2005). The Tsunami’s Impact on Women. Oxfam Briefing Note. http://www. 
oxfam.org.uk/what_we_do/issues/conflict_disasters/bn_tsunami_women.htm (last 
accessed 11 June 2007) 
Panayotou, T. (1994). Economic Instruments for environmental Management and 
Sustainable Development. Environmental Economics series Paper No.1, United Nations 
Environment Programme, Nairobi 
Peiris, J., Guan, Y. and Yuen, K. (2004). Severe acute respiratory syndrome. In Nature 
Medicine 10 (12):S88- S97 
Pelling, M. and Uitto, J. (2001). Small island developing states: natural disaster 
vulnerability and global change. In Environmental Hazards 3:49-62 
Peterson, D. (2003). Eating Apes. University of California Press, London 
Prakash, A. (2000). Responsible Care: An Assessment. In Business and Society 
39(2):183-209 
Rahnema, M. (Ed.) (1997). The Post-Development Reader. Zed Books, London 
Russett, B. and Oneal, J. (2001). Triangulating Peace: Democracy, Interdependence, 
and International Organizations, The Norton Series in World Politics. W. W. Norton and 
Company, London 
Sen, A. (1985). Commodities and Capabilities, Oxford University Press, Oxford 
Sen, A. (1992). Inequality Re-examined. Clarendon Press, Oxford 
Sen, A. (1999). Development as Freedom. Oxford University Press, Oxford 
Shiva, V. (1991). The Violence of the Green Revolution: Third World Agriculture, 
Ecology and Politics. Zed Books, London 
Singer, P. (2002). One World. Yale University Press, London 
Smith, K. (2006). Oil from bombed plant left to spill. In Nature 442:609 
36 SECTION A: OVERVIEW 
Solow, R. M. (1991), Sustainability: An Economist’s Perspective. The Eighteen J. 
Seward Johnson Lecture to the Marine Policy Center, Woods Hole Oceanographic 
Insitution. In Economics of the Environment: Selected Readings (ed. R. Dorfman and 
N.s Dorfman) 179-187. Norton, New York, NY 
D’Souza, M. and Lobo, C. (2004). Watershed Development, Water Management 
and the Millennium Development Goals. Paper presented at the Watershed Summit, 
Chandigarh, November 25-27, 2004. Watershed Organization Trust, Ahmednagar 
Spencer, D. (2001). Will They Survive? Prospects for Small farmers in sub-Saharan 
Africa. Paper Presented in Vision 2020: Sustainable food Security for All by 2020. 
International Conference Organized by the International Food Policy Research Institute 
(IFPRI), September 4-6, 2001, Bonn 
Speth, J. (2004). Red Sky at Morning: America and the Crisis of the Global 
Environment. Yale University Press, New Haven and London 
Stefano, P., Von Ritter, K. and Bishop, J. (2004). Assessing the Economic Value of 
Ecosystem Conservation. Environment Development Paper No.101. The World Bank, 
Washington, DC 
Stohr, W. (2001). Introduction. In New Regional Development Paradigms: 
Decentralization, Governance and the New Planning for Local-Level Development. (ed. 
Stohr, W., Edralin, J. and Mani, D). Contributions in Economic History Series (225). 
Published in cooperation with the United Nations and the United Nations Centre for 
Regional Development. Greenwood Press, Westport, CT 
UN (2000). United Nations Millennium Declaration. United Nations, New York, NY 
http://www.un.org/millennium/declaration/ares552e.htm (last accessed 1 May 
2007) 
UN (2002). Report of the World Summit on Sustainable Development. Johannesburg, 
South Africa, 26 August - 4 September. A/CONF.199/20. United Nations, New 
York, NY 
UN(2004). Human Rights and Poverty Reduction. A conceptual framework. United 
Nations Office of the High Commissioner for Human Rights. United Nations, New York 
and Geneva 
UN (2006). Trends in Total Migrant Stock: The 2005 Revision. Population Division of 
the Department of Economic and Social Affairs of the United Nations Secretariat, New 
York, NY http://www.un.org/esa/population/publications/migration/UN_Migrant_ 
Stock_Documentation_2005.pdf (last accessed 1 May 2007) 
UNAIDS (2006). 2006 Report on Global AIDS Epidemic. United Nations Programme 
on HIV/AIDS, Geneva 
UNDP (2004). Human Development Report 2001: Making New Technologies Work for 
Human Development. United Nations Development Programme, New York, NY 
UNDP (2005a). Environmental Sustainability in 100 Millennium Development Goal 
Country Report. United Nations Development Programme, New York, NY 
UNDP (2005b) Human Development Report 2005: International Cooperation at a 
Crossroads. United Nations Development Programme, New York, NY 
UNDP (2006) Human Development Report 2006. Beyond Scarcity: power, poverty and 
the global water crisis. United Nations Development Programme, New York, NY 
UNEP (2002). Global Environment Outlook (GEO-3). United Nations Environment 
Programme, Nairobi 
UNEP (2004b). GEO Year Book 2003. United Nations Environment Programme, 
Nairobi 
UNEP (2005a). GEO yearbook 2004/2005. United Nations Environment Programme, 
Nairobi 
UNEP (2005b). One Planet Many People: Atlas of our Changing Environment. United 
Nations Environment Programme, Nairobi 
UNEP (2006). Avian Influenza and the Environment: An Ecohealth Perspective. 
Paper prepared by David J. Rapport on behalf of UNEP, United Nations Environment 
Programme and EcoHealth Consulting, Nairobi 
UNESCO (2007). United Nations Decade of Education for Sustainable Development 
(2005-2014) http://portal.unesco.org/education/en/ev.php-URL_ID=27234&URL_ 
DO=DO_TOPIC&URL_SECTION=201.html/ (last accessed June 25) 
UNESCO-WWAP (2006). Water for People. Water for Life, The United Nations World 
Water Development Report. United Nations Educational, Scientific and Cultural 
Organization, Paris and Berghahn Books, Oxford and New York, NY 
UN-Habitat (2006). State of the World’s Cities 2006/7. United Nations-Habitat, 
Nairobi 
UNHCR (2006a). Statistical Yearbook 2004 Country Data Sheets: Guinea. United 
Nations High Commission for Refugees, Geneva 
UNHCR (2006b). 2005 Global refugee trends statistical overview of populations of 
refugees, asylum-seekers, internally displaced persons, stateless persons, and other 
persons of concern to UNHCR. United Nations High Commission for Refugees, Geneva 
UNICEF (2006). Pneumonia: The forgotten killer of children. United Nations Childrens 
Fund and World Health Organization, New York, NY 
UNPD (2005). World Urbanisation Prospects: The 2005 Revision (in GEO Data Portal). 
UN Population Division, New York, NY http://www.un.org/esa/population/unpop. 
htm (last accessed 4 June 2007) 
UNPD (2007). World Population Prospects: The 2006 Revision (in GEO Data Portal). 
UN Population Division, New York, NY http://www.un.org/esa/population/unpop. 
htm (last accessed 4 June 2007) 
USGS (2006). Studying the Elwha River, Washington, in Preparation for Dam Removal. 
In Sound Waves Monthly Newsletter. US Geological Survey, Washington, DC http:// 
soundwaves.usgs.gov/2006/11/fieldwork3.html (last accessed 12 June 2007) 
Van Oostdam, J., Donaldson, S., Feeley, M., Arnold, D., Ayotte, P., Bondy, G., Chan, 
L., Dewaily, E., Furgal, C.M., Kuhnlein, H., Loring, E., Muckle, G., Myles, E., Receveur, 
O., Tracy, B., Gill, U., Kalhok, S. (2005). Human health implications of environmental 
contaminants in Arctic Canada: A review. In Science of the Total Environment 
351–352:165–246 
Watson, R., Zinyower, M. and Dokken, D. (eds.) (1997). The regional impacts of 
climate change: an assessment of vulnerability. Summary for Decision Makers. Special 
Report of IPCC Working Group II. Intergovernmental Panel on Climate Change 
WBCSD (2007). Then & Now: Celebrating the 20th Anniversary of the “Brundtland 
Report” – 2006 WBCSD Annual Review. World Business Council for Sustainable 
Development, Geneva 
WCED (1987). Our Common Future. Oxford University Press, Oxford 
WHO (2000). Guidelines for Air Quality. WHO/SDE/OEH/00.02, World Health 
Organization, Geneva 
WHO (2002) The World Health Report. Reducing risks, promoting healthy life. World 
Health Organization, Geneva 
WHO (2006). Preventing disease through healthy environments: Towards an estimate 
of the environmental burden of disease. World Health Organization, Geneva 
WHO and UNICEF (2004). Meeting the MDG drinking-water and sanitation target: 
A mid-term assessment of progress. World Health Organization and United Nations 
Children’s Fund, Geneva and New York, NY 
Wolfe, N., Escalante, A., Karesh, W., Kilbourn, A., Spielman, A. and Lal, A. (1998). 
Wild Primate Populations in Emerging Infectious Disease Research: The Missing Link? In 
Emerging Infectious Diseases 4 (2):148-159 
Wolfe, N., Heneine, W., Carr, J., Garcia, A., Shanmugam, V., Tamoufe, U., Torimiro, J., 
Prosser, T., LeBreton, M., Mpoudi-Ngole, E., McCutchan, F., Birx, D., Folks, T., Burke, D. 
and Switzer, W. (2005). Emergence of unique primate T-lymphotropic viruses among 
central African bushmeat hunters. In Proceedings of the National Academy of Sciences 
102 (22):7994 – 7999 
Wolfe, N., Switzer. W., Carr, J., Bhullar, V., Shanmugam, V., Tamoufe, U., Prosser, A., 
Torimiro, J., Wright, A., Mpoudi-Ngole, E., McCutchan, F., Birx. D., Folks, T., Burke, 
D. and Heneine, W. (2004). Naturally acquired simian retrovirus infections in central 
African hunters. In The Lancet 363:932- 937 
Wood, W.B. (2001). Ecomigration: Linkages between environmental change and 
migration. In Zolberg, A.R. and Benda, P. M.(eds.) Global Migrants, Global Refugees. 
Berghahn, Oxford 
World Bank (2005). The Little Data Book 2005. The World Bank, Washington, DC 
World Bank (2006a). Where is the Wealth of Nations? Measuring Capital for the 21st 
Century. The World Bank, Washington, DC 
World Bank (2006b). World Development Indicators 2006 (in GEO Data Portal). The 
World Bank, Washington, DC 
World Bank and Wildlife Conservation Society (2006). The Silent Steppe: the Illegal 
Wildlife Trade Crisis. The World Bank, Washington DC 
WTO (2006). World Trade Report 2006: Exploring the Links Between Subsidies, Trade 
and the WTO. World Trade Organization, Geneva 
WRI (2005). World Resources 2005: The Wealth of the Poor – Managing Ecosystems 
to Fight Poverty. World Resources Institute in collaboration with the United Nations 
Development Programme, the United Nations Environment Programme and The World 
Bank. World Resources Institute, Washington, DC

More Related Content

PPTX
Sustainable development in environment studies
DOC
Principles of sustainable development
PDF
Climate change in bd termpaper
PPTX
Sustainable Development and Climate Change
PPTX
PDF
Natural Disaster in Bangladesh
PPTX
Population policies
PPTX
World Environment Day Celebration 2020 - Biodiversity
Sustainable development in environment studies
Principles of sustainable development
Climate change in bd termpaper
Sustainable Development and Climate Change
Natural Disaster in Bangladesh
Population policies
World Environment Day Celebration 2020 - Biodiversity

What's hot (20)

PPT
Disaster management in india
PDF
Sustainable development
PPTX
Environmental Education
PPTX
Introduction to sustainable develpment
PDF
Climate Risk and Vulnerability Assessment (and Identifying Adaptation Options)
 
PPTX
Environment and society
PDF
Climate change and bd
PPTX
Disaster Management in Bangladesh: Risk Reduction and Challenges
PDF
Analysis and Review of EIA of Padma Multipurpose Bridge Project in Bangladesh
PPTX
Sustainable development
PPTX
Presentation on bangladesh environmental policy (1992)
PDF
Hyogo Framework of Actions for Disaster Preparedness: Bangladesh Perspective
PPTX
Environment
PPTX
Salinity risk assessment in bangladesh
PPT
Role of NGO's in Sustainable Development (Sustainability in 21st Century)
PPTX
Relationship between environment and society
PDF
Climate Justice
PPTX
Onset of fertility transition by Tim Dyson and Mike Murphy
PPT
The Kyoto Protocol
PPTX
Climate change
Disaster management in india
Sustainable development
Environmental Education
Introduction to sustainable develpment
Climate Risk and Vulnerability Assessment (and Identifying Adaptation Options)
 
Environment and society
Climate change and bd
Disaster Management in Bangladesh: Risk Reduction and Challenges
Analysis and Review of EIA of Padma Multipurpose Bridge Project in Bangladesh
Sustainable development
Presentation on bangladesh environmental policy (1992)
Hyogo Framework of Actions for Disaster Preparedness: Bangladesh Perspective
Environment
Salinity risk assessment in bangladesh
Role of NGO's in Sustainable Development (Sustainability in 21st Century)
Relationship between environment and society
Climate Justice
Onset of fertility transition by Tim Dyson and Mike Murphy
The Kyoto Protocol
Climate change
Ad

Similar to Environment for development (20)

PDF
Sustainable development
PDF
Environment the problem
PDF
Environment the problem
PDF
Report of the world commission on environment and development
PDF
Report of the world commission on environment and development
PDF
PDF
hazards of industrialisation and urbanisation
PDF
Sustainable Development
PDF
hazards of industrialisation and urbanisation
PDF
04 HAZARDS OF INDUSTRIALISATION AND URBANISATION.pdf
PPTX
Concept of sustainability and sustainable development
PDF
Sustainable Development
PDF
What is sustainable development
PPTX
Sustainable Development: An Introduction
PDF
environment
PDF
From Resource Scarcity To Ecological Security Pirages Dennis Cousins
PDF
Sustainable development
PDF
Brundtland report
PDF
Brundtland report
PDF
Sustainable Development: a controversial concept
Sustainable development
Environment the problem
Environment the problem
Report of the world commission on environment and development
Report of the world commission on environment and development
hazards of industrialisation and urbanisation
Sustainable Development
hazards of industrialisation and urbanisation
04 HAZARDS OF INDUSTRIALISATION AND URBANISATION.pdf
Concept of sustainability and sustainable development
Sustainable Development
What is sustainable development
Sustainable Development: An Introduction
environment
From Resource Scarcity To Ecological Security Pirages Dennis Cousins
Sustainable development
Brundtland report
Brundtland report
Sustainable Development: a controversial concept
Ad

Recently uploaded (20)

PDF
4_Key Concepts Structure and Governance plus UN.pdf okay
PDF
oil palm convergence 2024 mahabubnagar.pdf
PDF
Item # 3 - 934 Patterson Final Review.pdf
PDF
CXPA Finland Webinar: Rated 5 Stars - Delivering Service That Customers Truly...
PPTX
26.1.2025 venugopal K Awarded with commendation certificate.pptx
PPTX
11Sept2023_LTIA-Cluster-Training-Presentation.pptx
PDF
PPT - Primary Rules of Interpretation (1).pdf
PPTX
BHARATIYA NAGARIKA SURAKSHA SAHMITA^J2023 (1).pptx
PPTX
Nur Shakila Assesmentlwemkf;m;mwee f.pptx
PDF
buyers sellers meeting of mangoes in mahabubnagar.pdf
PDF
Items # 6&7 - 900 Cambridge Oval Right-of-Way
PPTX
GOVERNMENT-ACCOUNTING1. bsa 4 government accounting
PPTX
Portland FPDR Oregon Legislature 2025.pptx
PDF
PPT Item # 2 -- Announcements Powerpoint
PPTX
Introduction_to_the_Study_of_Globalization.pptx
PDF
Item # 5 - 5307 Broadway St final review
DOCX
Alexistogel: Solusi Tepat untuk Anda yang Cari Bandar Toto Macau Resmi
PDF
Creating Memorable Moments_ Personalized Plant Gifts.pdf
PDF
26.1.2025 venugopal K Awarded with commendation certificate.pdf
PDF
Item # 2 - 934 Patterson Specific Use Permit (SUP)
4_Key Concepts Structure and Governance plus UN.pdf okay
oil palm convergence 2024 mahabubnagar.pdf
Item # 3 - 934 Patterson Final Review.pdf
CXPA Finland Webinar: Rated 5 Stars - Delivering Service That Customers Truly...
26.1.2025 venugopal K Awarded with commendation certificate.pptx
11Sept2023_LTIA-Cluster-Training-Presentation.pptx
PPT - Primary Rules of Interpretation (1).pdf
BHARATIYA NAGARIKA SURAKSHA SAHMITA^J2023 (1).pptx
Nur Shakila Assesmentlwemkf;m;mwee f.pptx
buyers sellers meeting of mangoes in mahabubnagar.pdf
Items # 6&7 - 900 Cambridge Oval Right-of-Way
GOVERNMENT-ACCOUNTING1. bsa 4 government accounting
Portland FPDR Oregon Legislature 2025.pptx
PPT Item # 2 -- Announcements Powerpoint
Introduction_to_the_Study_of_Globalization.pptx
Item # 5 - 5307 Broadway St final review
Alexistogel: Solusi Tepat untuk Anda yang Cari Bandar Toto Macau Resmi
Creating Memorable Moments_ Personalized Plant Gifts.pdf
26.1.2025 venugopal K Awarded with commendation certificate.pdf
Item # 2 - 934 Patterson Specific Use Permit (SUP)

Environment for development

  • 1. A Section Overview Chapter 1 Environment for Development
  • 2. “The ‘environment’ is where we live; and development is what we all do in attempting to improve our lot within that abode. The two are inseparable.” Our Common Future
  • 3. Chapter1 Environment for Development Coordinating lead authors: Diego Martino and Zinta Zommers Lead authors: Kerry Bowman, Don Brown, Flavio Comim, Peter Kouwenhoven, Ton Manders, Patrick Milimo, Jennifer Mohamed-Katerere, and Thierry De Oliveira Contributing authors: Dan Claasen, Simon Dalby, Irene Dankelman, Shawn Donaldson, Nancy Doubleday, Robert Fincham, Wame Hambira, Sylvia I. Karlsson, David MacDonald, Lars Mortensen, Renata Rubian, Guido Schmidt-Traub, Mahendra Shah, Ben Sonneveld, Indra de Soysa, Rami Zurayk, M.A. Keyzer, and W.C.M. Van Veen Chapter review editor: Tony Prato Chapter coordinators: Thierry De Oliveira, Tessa Goverse, and Ashbindu Singh Credit: fotototo/Still Pictures
  • 4. Main messages It is 20 years since the report of the World Commission on Environment and Development (WCED), Our Common Future, emphasized the need for a sustainable way of life which not only addresses current environmental challenges but also ensures a secure society well into the future. This chapter analyses the evolution of such ideas as well as global trends in relation to environment and socio-economic development. The following are its main messages: The world has changed radically since 1987 – socially, economically and environmentally. Global population has grown by more than 1.7 billion, from about 5 billion people. The global economy has expanded and is now characterized by increasing globalization. Worldwide, GDP per capita (purchasing power parity) has increased from US$5 927 in 1987 to US$8 162 in 2004. However, growth has been distributed unequally between regions. Global trade has increased during the past 20 years, fuelled by globalization, better communication, and low transportation costs. Technology has also changed. Communications have been revolutionized with the growth of telecommunications and the Internet. Worldwide, mobile phone subscribers increased from 2 people per 1 000 in 1990 to 220 per 1 000 in 2003. Internet use increased from 1 person per 1 000 in 1990 to 114 per 1 000 in 2003. Finally, political changes have also been extensive. Human population and economic growth has increased demand on resources. The World Commission on Environment and Development (WCED) recognized 20 years ago that the environment, economic and social issues are interlinked. It recommended that the three be integrated into development decision making. In defining sustainable development, the Commission acknowledged the need for both intra- and intergenerational equity – development that meets not only today’s human needs but also those of more people in the future. Changing drivers, such as population growth, economic activities and consumption patterns, have placed increasing pressure on the environment. Serious and persistent barriers to sustainable development remain. In the past 20 years, there has been limited integration of environment into development decision making. Environmental degradation is therefore undermining development and threatens future development progress. Development is a process that enables people to better their well-being. Long-term development can only be achieved through sustainable management of various assets: financial, material, human, social and natural. Natural assets, including water, soils, plants and animals, underpin people’s livelihoods. Environmental degradation also threatens all aspects of human well-being. Environmental degradation has been demonstrably linked to human health problems, including some types of cancers, vector-borne diseases, emerging animal to human disease transfer, nutritional deficits and respiratory illnesses. The environment provides essential material assets and an economic base for human endeavour. Almost half the jobs worldwide depend on fisheries, forests or agriculture. Non-sustainable use of natural resources, including land, water, forests and fisheries, can threaten individual livelihoods as well as local, national and international economies. The environment can play a significant role in contributing to development and human well-being, but can also increase human vulnerability, causing human migration and insecurity, such as in the case of storms, droughts or environmental
  • 5. mismanagement. Environmental scarcity can foster cooperation, but also contribute to tensions or conflicts. Environmental sustainability, Millennium Development Goal 7, is critical to the attainment of the other MDG goals. Natural resources are the basis of subsistence in many poor communities. In fact, natural capital accounts for 26 per cent of the wealth of low-income countries. Up to 20 per cent of the total burden of disease in developing countries is associated with environmental risks. Poor women are particularly vulnerable to respiratory infections related to exposure to indoor air pollution. Acute respiratory infections are the leading cause of death in children, with pneumonia killing more children under the age of five than any other illness. A combination of unsafe water and poor sanitation is the world’s second biggest killer of children. About 1.8 million children die annually and about 443 million school days are missed due to diarrhoea. Clean water and air are powerful preventative medicines. Sustainable management of natural resources contributes to poverty alleviation, helps reduce diseases and child mortality, improves maternal health, and can contribute to gender equity and universal education. Some progress towards sustainable development has been made since 1987 when the WCED report, Our Common Future, was launched. The number of meetings and summits related to the environment and development has increased (for example, the 1992 Rio Earth Summit and the 2002 World Summit on Sustainable Development), and there has been a rapid growth in multilateral environmental agreements (for example, the Kyoto Protocol and the Stockholm Convention on Persistent Organic Pollutants). Sustainable development strategies have been implemented at local, national, regional and international levels. An increasing number of scientific assessments (for example, the Intergovernmental Panel on Climate Change) have contributed to a greater understanding of environmental challenges. In addition, proven and workable solutions have been identified for environmental problems that are limited in scale, highly visible and acute, (for example, industrial air and water pollution, local soil erosion and vehicle exhaust emission). However, some international negotiations have stalled over questions of equity and responsibility sharing. Interlinkages between drivers and pressures on the global environment make solutions complex. As a result, action has been limited on some issues, for example, climate change, persistent organic pollutants, fisheries management, invasive alien species and species extinction. Effective policy responses are needed at all levels of governance. While proven solutions continue to be used, action should also be taken to address both the drivers of change and environmental problems themselves. A variety of tools that have emerged over the past 20 years may be strategic. Economic instruments, such as property rights, market creation, bonds and deposits, can help correct market failures and internalize costs of protecting the environment. Valuation techniques can be used to understand the value of ecosystem services. Scenarios can provide insights on the future impacts of policy decisions. Capacity building and education are critical to generate knowledge and inform the decision making process. Society has the capacity to make a difference in the way the environment is used to underpin development and human well-being. The following chapters highlight many of the challenges society faces today and provides signposts towards sustainable development.
  • 6. INTRODUCTION Imagine a world in which environmental change threatens people’s health, physical security, material needs and social cohesion. This is a world beset by increasingly intense and frequent storms, and by rising sea levels. Some people experience extensive flooding, while others endure intense droughts. Species extinction occurs at rates never before witnessed. Safe water is increasingly limited, hindering economic activity. Land degradation endangers the lives of millions of people. This is the world today. Yet, as the World Commission on Environment and Development (Brundtland Commission) concluded 20 years ago “humanity has the ability to make development sustainable.” The fourth Global Environment Outlook highlights imperative steps needed to achieve this vision. The fourth GEO assesses the current state of the world’s atmosphere, land, water and biodiversity, providing a description of the state of environment, and demonstrating that the environment is essential for improving and sustaining human well-being. It also shows that environmental degradation is diminishing the potential for sustainable development. Policies for action are highlighted to facilitate alternative development paths. This chapter examines developments since the landmark 1987 Brundtland Commission report – Our Common Future – placed sustainable development much higher on the international policy agenda. It examines institutional developments and changes in thought since the mid-1980s, and explores the relationships involving environment, development and human well-being, reviews major environmental, social and economic trends, and their impacts on environment and human well-being, and provides options to help achieve sustainable development. Subsequent chapters will analyse of environmental changes in the atmosphere, land, water and biodiversity, both at global and regional levels, and will highlight human vulnerability and strategic policy interlinkages for effective responses. Positive developments since 1987 are described. These include progress towards meeting the goals of the Montreal Protocol, and the reduction in emissions of 6 SECTION A: OVERVIEW chemicals that deplete the stratospheric ozone layer. Yet, the chapters also highlight current environmental trends that threaten human well-being: ® In some cases, climate change is having severe effects on human health, food production, security and resource availability. ® Extreme weather conditions are having an increasingly large impact on vulnerable human communities, particularly the world’s poor. ® Both indoor and outdoor pollution is still causing many premature deaths. ® Land degradation is decreasing agricultural productivity, resulting in lower incomes and reduced food security. ® Decreasing supplies of safe water are jeopardizing human health and economic activity. ® Drastic reductions of fish stocks are creating both economic losses and a loss of food supply. ® Accelerating species extinction rates are threatening the loss of unique genetic pools, possible sources for future medical and agricultural advances. Choices made today will determine how these threats will unfold in the future. Reversing such adverse environmental trends will be an immense challenge. Ecosystem services collapse is a distinct possibility if action is not taken. Finding solutions to these problems today is therefore urgent. This chapter provides a message for action today: The Earth is our only home. Its well-being, and our own, is imperilled. To ensure long-term well-being, we must take an alternative approach to development, one that acknowledges the importance of environment. OUR COMMON FUTURE: EVOLUTION OF IDEAS AND ACTIONS Two decades ago the Brundtland Commission report – Our Common Future – addressed the links between development and environment, and challenged policy-makers to consider the interrelationships among environment, economic and social issues when it comes to solving global problems. The report examined emerging global challenges in: ® population and human resources; ® food security; ® species and ecosystems; ® energy; ® industry; and ® urbanization.
  • 7. Gro Harlem Brundtland introduces to the General Assembly, the report of the World Commission on Environment and Development in 1987, which she chaired. The work of the Brundtland Commission challenged policy-makers to consider the interrelationships among environment, economic and social issues in efforts to solve global problems. Credit: UN Photo/Milton Grant ENV I RONMENT FOR DE V E LOPMENT 7 The commission recommended institutional and legal changes in six broad areas to address these challenges: ® getting at the sources; ® dealing with the effects; ® assessing global risks; ® making informed choices; ® providing the legal means; and ® investing in our future. Recommendations emphasized the expansion of international institutions for cooperation, and the creation of legal mechanisms for environmental protection and sustainable development, and also stressed the links between poverty and environmental degradation. They also called for increased capacity to assess and report on risks of irreversible damage to natural systems, as well as threats to human survival, security and well-being. The work of the commission was built on the foundation of, among others, the 1972 UN Conference on the Human Environment in Stockholm and the 1980 World Conservation Strategy, which emphasized conservation as including both protection and the rational use of natural resources (IUCN and others 1991). The Brundtland Commission is widely attributed with popularizing sustainable development internationally (Langhelle 1999). It defined sustainable development as “development that meets the needs of the present generation without compromising the ability of future generations to meet their own needs.” The commission further explained that, “the concept of sustainable development implies limits – not absolute limits but limitations imposed by the present state of technology and social organization on environmental resources and by the ability of the biosphere to absorb the effects of human activities.” It was argued that, “technology and social organization can be both managed and improved to make way for a new era of economic growth” (WCED 1987). The most immediate and perhaps one of the most significant results of Our Common Future was the organization of the UN Conference on Environment and Development (UNCED), also known as the Earth Summit, which gathered many heads of state in Rio de Janeiro in 1992. Not only did this meeting bring together 108 government leaders, more than 2 400 representatives from non-governmental organizations (NGOs) attended, and 17 000 people participated in a parallel NGOs event. The Earth Summit strengthened interaction among governments, NGOs and scientists, and fundamentally changed attitudes towards governance and the environment. Governments were encouraged to rethink the concept of economic development, and to find ways to halt the destruction of natural resources and reduce pollution of the planet. The summit resulted in several important steps towards sustainable development. Through the adoption of the Rio Declaration and Agenda 21, it helped formalize an international institutional framework to implement the ideas highlighted in Our Common Future. The Rio Declaration contains 27 principles that nations agreed to follow to achieve the goals articulated by the
  • 8. Brundtland Commission. Key commitments in the Rio Declaration included integration of environment and development in decision making, provision for polluters to pay for costs of pollution, recognition of common but differentiated responsibilities, and application of the precautionary approach to decision making. Agenda 21 articulated a comprehensive plan of action towards sustainable development. It contains 40 chapters, which can be divided into four main areas: ® social and economic issues, such as poverty, human health and population; ® conservation and management of natural resources including the atmosphere, forests, biological diversity, wastes and toxic chemicals; ® the role of nine major groups in implementing the sustainable development agenda (local authorities, women, farmers, children and youth, indigenous peoples, workers and trade unions, NGOs, the scientific and technological community, and business and industry); and ® means of implementation, including technology transfer, financing, science, education and public information. Embedded in these four main areas of Agenda 21 are the environmental challenges, as well as the broad governance issues highlighted in the Brundtland Commission report. As the blueprint for sustainable development, Agenda 21 remains the most significant non-binding instrument in the environmental field (UNEP 2002). Funding for the implementation of Agenda 21 was to be obtained from the Global Environment Facility (GEF). As a partnership involving the UNEP, UNDP and World Bank, GEF was established the year before the Earth Summit to mobilize resources for projects that seek to protect the environment. Since 1991, the GEF has provided US$6.8 billion in grants, and generated more than US$24 billion in co-financing from other sources to support about 2 000 projects that produce global environmental benefits in more than 160 developing countries and countries with economies in transition. GEF funds are contributed by donor countries, and in 2006, 32 countries pledged a total of US$3.13 billion to fund various environment-related initiatives over four years (GEF 2006). 8 SECTION A: OVERVIEW The turn of the century brought a sense of urgency to attempts to address environment and development challenges. World leaders sought to ensure a world free from want. In the Millennium Declaration, adopted in 2000, world leaders committed to free their people from the “threat of living on a planet irredeemably spoilt by human activities, and whose resources would no longer be sufficient for their needs” (UN 2000). The Millennium Summit, adopted the declaration and created time-bound goals and targets – the Millennium Development Goals (MDGs) – to better human well-being. Two years after the Millennium Declaration and a decade after the Rio Earth Summit, world leaders reaffirmed sustainable development as a central goal on the international agenda at the 2002 Johannesburg World Summit on Sustainable Development (WSSD). More than 21 000 participants attended the summit, along with representatives of more than 191 governments. The UN Secretary-General designated five priority areas for discussion: water, including sanitation, energy, health, agriculture and biodiversity. These became to be known by the acronym WEHAB. These issues can also be traced back to initiatives such as the Brundtland Commission. The WSSD outcomes include the Johannesburg Declaration on Sustainable Development, and a 54-page plan of implementation. World leaders committed themselves, “to expedite the achievement of the time-bound, socio-economic and environmental targets” contained within the Plan of Implementation (Johannesburg Declaration on Sustainable Development). This historic summit also achieved new commitments on water and sanitation, poverty eradication, energy, sustainable production and consumption, chemicals, and management of natural resources (UN 2002). The last 20 years has also seen a growth in the number of scientific assessments, such as the Intergovernmental Panel on Climate Change, the Millennium Ecosystem Assessment and the Global Environment Outlook. The Intergovernmental Panel on Climate Change was established in 1988 to assess on an objective, open and transparent basis the scientific, technical and socio-economic information relevant to climate change. In 2007, the IPCC released its Fourth Assessment Report. The Millennium Ecosystem Assessment was called for by the then UN Secretary-General Kofi Annan, to assess the
  • 9. ENV I RONMENT FOR DE V E LOPMENT 9 consequences of ecosystem change for human well-being. These scientific assessments reflect the work of thousands of experts worldwide, and have led to greater understanding of environmental problems. As a result of the conferences and assessments highlighted above, a diversity of multilateral environmental agreements (MEAs) have been adopted (see Figure 1.1), and these and several others are analysed in relevant chapters throughout this report. The Convention on Biological Diversity (CBD) was signed by 150 government leaders at the Rio Earth Summit. The CBD sets out commitments for conserving biodiversity, the sustainable use of its components, and fair and equitable sharing of its benefits. The Cartagena Protocol on Biosafety is based on the precautionary approach from the Rio Declaration. Principle 15 of the Rio Declaration states that, “where there are threats of serious and irreversible damage lack of full scientific certainty shall not be used as a reason for postponing cost effective measures to prevent biological degradation” (UNGA 1992). The Protocol promotes biosafety in the handling, transfer and use of living modified organisms. Two agreements that have drawn significant attention during the last 20 years are the Montreal Protocol to the Vienna Convention on Substances that Deplete the Ozone Layer and the Kyoto Protocol to the UN Framework Convention on Climate Change. The Montreal Protocol, which became effective in 1989 and had 191 parties at the beginning of 2007, has helped decrease or stabilize atmospheric concentrations of many of the ozone-depleting substances, including chlorofluorocarbons. The protocol is regarded as one of the most successful international agreements to date. By contrast, despite the urgency of climate change, it has been much more difficult to get some countries responsible for significant emissions of greenhouse gases to ratify the Kyoto Protocol. Environmental governance has changed since the Brundtland Commission. Today, a broader scope of issues related to environment and development are discussed. The issues of trade, economic development, good governance, transfer of technology, science and education policies, and globalization, which links them together, have become even more central to sustainable development. Different levels of government participate in environmental policy. The post-WCED period saw a strong increase in sub-national and local government action, for example, through local Agenda 21 processes. The Johannesburg Plan of Implementation stressed that the role of national policies and development strategies “cannot be overemphasized.” It also strengthened the role of the regional level, Figure 1.1 Ratification of major multilateral environmental agreements Source: GEO Data Portal, compiled from various MEA secretariats Number of parties 200 175 125 75 50 25 0 1971 2007 100 1981 Basel CBD CITES CMS World Heritage Kyoto 1979 1983 1975 Ozone 1985 2003 1999 1989 1995 1987 1991 1997 2001 1993 2005 1997 Ramsar Rotterdam Stockholm UNCCD UNCLOS UNFCCC Cartagena 150 1973
  • 10. for example by giving the regional UN economic commissions new tasks, and establishing a regional preparation process for the Commission on Sustainable Development (CSD) (UN 2002). The number of non-governmental stakeholders involved in environmental governance has grown considerably, with organizations playing key roles from local to global levels. NGOs and advocacy groups devoted to public interest and environmental causes have multiplied exponentially, particularly in countries undertaking democratic transitions (Carothers and Barndt 2000). The private sector should also take action to help protect the environment. Even though business was “given little attention by the WCED …, more boards and executive committees are trying to consider all dimensions of their impacts at once, on the same agenda, in the same room” (WBCSD 2007). As consumer demand for “green” products arose, some businesses developed voluntary environmental codes, or followed codes developed by non-governmental Box 1.1 Environment as the foundation for development 10 SECTION A: OVERVIEW organizations and governments (Prakash 2000). Other companies began to monitor and report on their sustainability impacts. A study by eight corporate leaders on what business success would look like in the future concluded that it would be tied to helping society cope with challenges such as poverty, globalization, environmental decline and demographic change (WBCSD 2007). Finally, decision making is increasingly participatory. Stakeholder groups interact with each other and with governments through networks, dialogues and partnerships. Interaction among groups at local, national and global levels was institutionalized in the action plans of UNCED and WSSD. Chapter 37 of Agenda 21 urged countries to involve all possible interest groups in building national consensus on Agenda 21 implementation, and Chapter 28 encouraged local authorities to engage in dialogue with their citizens. Environment as the foundation for development Before the Brundtland Commission, “development progress” was associated with industrialization, and measured solely by economic activity and increases in wealth. Environmental protection was perceived by many as an obstacle to development. However, Our Common Future recognized “environment or development” as a false dichotomy. Focus shifted to “environment and development,” and then to “environment for development (see Box 1.1).” Principle 1 of Agenda 21 states: “Human beings are at the centre of concerns for sustainable development. They are entitled to a healthy and productive life in harmony with nature.” The normative framework for human development is reflected by the MDGs (UNDP 2006). In signing on to the MDGs, nations explicitly recognized that achieving Goal 7 on environmental sustainability is key to achieving poverty eradication. However, environmental issues are not highly integrated into other MDGs (UNDP 2005a). A healthy environment is essential for achieving all the goals (see Table 1.1). To achieve real progress, the interlinkages between MDG 7 and the other MDGs need to be acknowledged and integrated into all forms of planning. While a healthy environment can support development, the relationship is not always reciprocal. Many alternative views exist on the benefits and disadvantages of modern development (Rahnema 1997). It has been argued that development is destructive, even violent, to nature (Shiva 1991). As GEO-4 illustrates, past development practices have often not been beneficial to the environment. However, opportunities exist to make development sustainable. Environmental degradation due to development raises deep ethical questions that go beyond economic Development is the process of furthering people’s well-being. Good development entails: ® increasing the asset base and its productivity; ® empowering poor people and marginalized communities; ® reducing and managing risks; and ® taking a long-term perspective with regard to intra- and intergenerational equity. The environment is central to all four of these requirements. Long-term development can only be achieved through sustainable management of various assets: financial, material, human, social and natural. Natural assets, including water, soils, plants and animals, underpin the livelihoods of all people. At the national level, natural assets account for 26 per cent of the wealth of low-income countries. Sectors such as agriculture, fishery, forestry, tourism and minerals provide important economic and social benefits to people. The challenge lies in the proper management of these resources. Sustainable development provides a framework for managing human and economic development, while ensuring a proper and optimal functioning over time of the natural environment. Sources: Bass 2006, World Bank 2006a
  • 11. Livelihood strategies and food security of the poor often depend directly on healthy ecosystems, and the diversity of goods and ecological services they provide. Natural capital accounts for 26 per cent of the wealth of low-income countries. Climate change affects agricultural productivity. Ground-level ozone damages crops. ENV I RONMENT FOR DE V E LOPMENT 11 Table 1.1 Links between the environment and the Millennium Development Goals Millennium Development Goal Selected environmental links 1. Eradicate extreme poverty and hunger cost-benefit ratios. The question of justice is perhaps the greatest moral question emerging in relation to environmental change and sustainable development. Growing evidence indicates that the burden of environmental change is falling far from the greatest consumers of environmental resources, who experience the benefits of development. Often, people living in poverty in the developing world, suffer the negative effects of environmental degradation. Furthermore, costs of environmental degradation will be experienced by humankind in future generations. Profound ethical questions are raised when benefits are extracted from the environment by those who do not bear the burden. Barriers to sustainable development Despite changes in environmental governance, and greater understanding of the links between environment and development, real progress towards sustainable development has been slow. Many governments continue to create policies concerned with environmental, economic and social matters as single issues. There is a continued failure to link environment and development in decision making (Dernbach 2002). As a result, development strategies often ignore the need to maintain the very ecosystem services on which long-term development goals depend. A notable example, made apparent in the aftermath of 2. Achieve universal primary education Cleaner air will decrease the illnesses of children due to exposure to harmful air pollutants. As a result, they will miss fewer days of school. Water-related diseases such as diarrhoeal infections cost about 443 million school days each year, and diminish learning potential. 3. Promote gender equality, and empower women Indoor and outdoor air pollution is responsible for more than 2 million premature deaths annually. Poor women are particularly vulnerable to respiratory infections, as they have high levels of exposure to indoor air pollution. Women and girls bear the brunt of collecting water and fuelwood, tasks made harder by environmental degradation, such as water contamination and deforestation. 4. Reduce child mortality Acute respiratory infections are the leading cause of death in children. Pneumonia kills more children under the age of 5 than any other illness. Environmental factors such as indoor air pollution may increase children’s susceptibility to pneumonia. Water-related diseases, such as diarrhoea and cholera, kill an estimated 3 million people/year in developing countries, the majority of whom are children under the age of five. Diarrhoea has become the second biggest killer of children, with 1.8 million children dying every year (almost 5 000/day). 5. Improve maternal health Indoor air pollution and carrying heavy loads of water and fuelwood adversely affect women’s health, and can make women less fit for childbirth and at greater risk of complications during pregnancy. Provision of clean water reduces the incidence of diseases that undermine maternal health and contribute to maternal mortality. 6. Combat major diseases Up to 20 per cent of the total burden of disease in developing countries may be associated with environmental risk factors. Preventative environmental health measures are as important and at times more cost-effective than health treatment. New biodiversity-derived medicines hold promises for fighting major diseases. 7. Ensure environmental sustainability Current trends in environmental degradation must be reversed in order to sustain the health and productivity of the world’s ecosystems. 8. Develop a global partnership for development Poor countries and regions are forced to exploit their natural resources to generate revenue and make huge debt repayments. Unfair globalization practices export their harmful side-effects to countries that often do not have effective governance regimes. Source: Adapted from DFID and others 2002, UNDP 2006, UNICEF 2006
  • 12. the 2005 Hurricane Katrina, is the failure of some government agencies to see the link between destruction of coastal wetlands and the increased vulnerability of coastal communities to storms (Travis 2005, Fischetti 2005). For many, acknowledging that environmental change could endanger future human well-being is inconvenient, as it requires an uncomfortable level of change to individual and working lives (Gore 2006). International negotiations on solutions to global environmental problems have frequently stalled over questions of equity (Brown 1999). For instance, in the case of climate change, international negotiations have slowed down over the question on how to share responsibilities and burden among nations, given different historic and current levels of national emissions. Providing widespread participation in sustainable development decision making called for by Agenda 21 has also raised significant challenges. The enormous diversity of issues that need to be considered in sustainable development policy making, together with aspirations for transparency, 12 SECTION A: OVERVIEW make public participation design daunting. If participation is treated superficially, and embodied merely as a quota of specified groups in decision making processes, it could easily be no more than “lip service.” The task of designing modern, cross-cutting, transparent, evidence-based interdisciplinary decision making is not only conceptually challenging, but also necessitates a huge increase in local capacity for democracy and decision making (MacDonald and Service 2007). Many social, economic and technological changes described later in this chapter have made implementation of the recommendations in Our Common Future difficult. As also illustrated in other chapters, changes such as a growing population and increased consumption of energy have had a huge impact on the environment, challenging society’s ability to achieve sustainable development. Finally, the nature of the environmental problems has influenced the effectiveness of past responses. Environmental problems can be mapped along a continuum from “problems with proven solutions” to “less known emerging (or persistent) problems” (Speth 2004). With problems with proven solutions, the cause-and- effect relationships are well known. The scale tends to be local or national. Impacts are highly visible and acute, and victims are easily identified. During the past 20 years, workable solutions have been identified for several such problems, for example industrial air and water pollution, local soil erosion, mangrove clearance for aquaculture, and vehicle exhaust emissions. However, progress has been limited on harder to manage environmental issues, which can also be referred to as “persistent” problems (Jänicke and Volkery 2001). These are deeply rooted structural problems, related to the ways production and consumption are conducted at the household, national, regional and global levels. Harder to manage problems tend to have multiple dimensions and be global in scale. Some of the basic science of cause-and- effect relationships is known, but often not enough to predict when a tipping point or a point of no return will be reached. There is often a need to implement measures on a very large-scale. Examples of such problems include global climate change, persistent organic pollutants and heavy metals, ground level ozone, acid rain, large-scale deterioration of fisheries, extinction of species, or introductions of alien species. Women and girls bear the brunt of collecting fuelwood, tasks made harder by environmental degradation. Credit: Christian Lambrechts
  • 13. ENV I RONMENT FOR DE V E LOPMENT 13 Awareness of the nature of an environmental problem provides a basis for creating strategies, targeting efforts, and finding and implementing a sustainable solution. Possible solutions to different types of environmental problems are introduced in the last section of this chapter, highlighted in the rest of the report, and discussed further in Chapter 10. HUMAN WELL-BEING AND THE ENVIRONMENT For sustainable development to be achieved, links between the environment and development must be examined. It is also important to consider the end point of development: human well-being. The evolution of ideas on development has made the concept of human well-being central to the policy debate. Human well-being is the outcome of development. Human well-being and the state of the environment are strongly interlinked. Establishing how environmental changes have impacts on human well-being, and showing the importance of environment for human well-being, are among the core objectives of this report. Defining human well-being Defining human well-being (see Box 1.2) is not easy, due to alternative views on what it means. Simply put, human well-being can be classified according to three views, each of which has different implications for the environment: ® The resources people have, such as money and other assets. Wealth is seen as conducive to well-being. This view is closely linked to the concept of weak sustainability, which argues that environmental losses can be compensated for by increases in physical capital (machines) (Solow 1991). The environment can only contribute to development as a means to promote economic growth. ® How people feel about their lives (their subjective views). Individuals’ assessments of their own living conditions take into account the intrinsic importance that environment has for life satisfaction. According to this view, people value the environment for its traditional or cultural aspects (Diener 2000, Frey and Stutzer 2005). ® What people are able to be and to do. This view focuses on what the environment allows individuals to be and to do (Sen 1985, Sen 1992, Sen 1999). It points out that the environment provides the basis for many benefits, such as proper nourishment, avoiding unnecessary morbidity and premature mortality, enjoying security and self-respect, and taking part in the life of the community. The environment is appreciated beyond its role as income generator, and its impacts on human well-being are seen as multidimensional. Human well-being is the extent to which individuals have the ability and the opportunity to live the kinds of lives they have reason to value. People’s ability to pursue the lives that they value is shaped by a wide range of instrumental freedoms. Human well-being encompasses personal and environmental security, access to materials for a good life, good health and good social relations, all of which are closely related to each other, and underlie the freedom to make choices and take action: ® Health is a state of complete physical, mental and social well-being, and not merely the absence of disease or illness. Good health not only includes being strong and feeling well, but also freedom from avoidable disease, a healthy physical environment, access to energy, safe water and clean air. What one can be and do include among others, the ability to keep fit, minimize health-related stress, and ensure access to medical care. ® Material needs relate to access to ecosystem goods-and-services. The material basis for a good life includes secure and adequate livelihoods, income and assets, enough food and clean water at all times, shelter, clothing, access to energy to keep warm and cool, and access to goods. ® Security relates to personal and environmental security. It includes access to natural and other resources, and freedom from violence, crime and wars (motivated by environmental drivers), as well as security from natural and human-caused disasters. ® Social relations refer to positive characteristics that define interactions among individuals, such as social cohesion, reciprocity, mutual respect, good gender and family relations, and the ability to help others and provide for children. Increasing the real opportunities that people have to improve their lives requires addressing all these components. This is closely linked to environmental quality and the sustainability of ecosystem services. Therefore, an assessment of the impact of the environment on individuals’ well-being can be done by mapping the impact of the environment on these different components of well-being. Box 1.2 Human well-being Sources: MA 2003, Sen 1999
  • 14. The evolution of these ideas has progressed from the first to the third, with increasing importance being given to the real opportunities that people have to achieve what they wish to be and to do. This new understanding of human well-being has several important aspects. First, multidimensionality is viewed as an important feature of human well-being. 14 SECTION A: OVERVIEW Consequently, the impact of the environment on human well-being is seen according to many different dimensions. Second, autonomy is considered a defining feature of people, and of well-being. Autonomy can be defined broadly as allowing people to make individual or collective choices. In other words, to know whether an individual is well requires considering his or her resources, subjective views, and the ability to choose and act. This concept of human well-being highlights the importance of understanding whether individuals are simply passive spectators of policy interventions, or, in fact, active agents of their own destiny. Context of human well-being The potential for individuals, communities and nations to make their own choices, and maximize opportunities to achieve security and good health, meet material needs and maintain social relations is affected by many interlinked factors, such as poverty, inequality and gender. It is important to note how these factors relate to each other, and to the environment. Poverty and inequality Poverty is understood as a deprivation of basic freedoms. It implies a low level of well-being, with such outcomes as poor health, premature mortality and morbidity, and illiteracy. It is usually driven by inadequate control over resources, discrimination (including by race or gender), and lack of access to material assets, health care and education (UN 2004). Inequality refers to the skewed distribution of an object of value, such as income, medical care or clean water, among individuals or groups. Unequal access to environmental resources remains an important source of inequality among individuals. Equity is the idea that a social arrangement addresses equality in terms of something of value. Distributive analysis is used to assess features of human well-being that are unequally distributed among individuals according to arbitrary factors, such as gender, age, religion and ethnicity. When an analysis of this distribution focuses on its lower end, it refers to poverty. Mobility When seen in a dynamic perspective, inequality and poverty are better understood through the concepts of social mobility and vulnerability. Mobility relates to the ability of people to move from one social group, class or level to another. Environmental degradation may be responsible for locking individuals within low-mobility paths, limiting opportunities to improve their own well-being. Vulnerability Vulnerability involves a combination of exposure and sensitivity to risk, and the inability to cope or adapt to environmental change. Most often, the poor are more vulnerable to environmental change. Broad patterns of vulnerability to environmental and socio-economic changes can be identified so that policy-makers can respond, providing opportunities for reducing Individuals’ assessments of their own living conditions take into account the intrinsic importance that the environment has for life satisfaction. Credit: Mark Edwards/Still Pictures
  • 15. Box 1.3 Ecosystem services Ecosystem services include provisioning services, such as food and water; regulating services, such as flood and disease control; cultural services, such as spiritual, recreational and cultural benefits; and supporting services, such as nutrient cycling that maintain the conditions for life on Earth (see Table 5.2 in Chapter 5 for details). ENV I RONMENT FOR DE V E LOPMENT 15 vulnerability, while protecting the environment. Chapter 7 assesses the vulnerability of the human-environment system to multiple stresses (drivers and pressures). Gender inequality An analysis of distributive impacts of the environment on human well-being cannot ignore features such as gender. Gender inequality is one of the most persistent inequalities in both developed and developing countries, with the majority of people living in poverty being women (UNDP 2005b). Women and girls often carry a disproportionate burden from environmental degradation compared to men. Understanding the position of women in society, and their relationship with the environment is essential for promoting development. In many cases, women and girls assume greater responsibilities for environmental management, but have subordinate positions in decision making (Braidotti and others 1994). Women need to be at the centre of policy responses (Agarwal 2000). At the same time, it is important to avoid stereotyping these roles, and to base responses on the complexities of local realities (Cleaver 2000). Environmental change and human well-being One of the main findings of the Millennium Ecosystem Assessment is that the relationship between human well-being and the natural environment is mediated by services provided by ecosystems (see Box 1.3). Changes to these services, as a result of changes in the environment, affect human well-being through impacts on security, basic material for a good life, health, and social and cultural relations (MA 2003). All people – rich and poor, urban and rural, and in all regions – rely on natural capital. The world’s poorest people depend primarily on environmental goods-and-services for their livelihoods, which makes them particularly sensitive and vulnerable to environmental changes (WRI 2005). Furthermore, many communities in both developing and developed countries derive their income from environmental resources, which include fisheries, non-timber forest products and wildlife. Health Shortly before the publication of Our Common Future, the nuclear accident at Chernobyl illustrated the catastrophic impact pollution can have on health. Twenty years later, as victims of Chernobyl still struggle with disease, the health of countless other people around the world continues to be affected by human-induced changes to the environment. Changes The relationship between human well-being and the natural environment is influenced by services provided by ecosystems. Credit: Joerg Boethling/Still Pictures Source: MA 2005a
  • 16. affecting provisioning services, including water, can influence human health. Changes affecting regulating services influence health via the distribution of disease transmitting insects or pollutants in water and air (MA 2003). Almost one-quarter of all diseases are caused by environmental exposure (WHO 2006). As described in Chapter 2, urban air pollution is one of the most widespread environmental problems, affecting health in almost all regions of the world. While Sources: Bell and others 2004, Brown 2006, Goodall 2005, Fa and others 2007, Karesh and others 2005, Leroy and others 2004, Li and others 2005, Peiris and others 2004, Peterson 2003, Wolfe and others 2004, Wolfe and others 2005 16 SECTION A: OVERVIEW air pollution has decreased in many industrialized countries, it has increased in other regions, particularly in Asia. Here, rapid population growth, economic development and urbanization have been associated with increasing use of fossil fuels, and a deterioration of air quality. WHO estimates that more than 1 billion people in Asian countries are exposed to air pollutant levels exceeding their guidelines (WHO 2000). In 2002, WHO estimated that more than 800 000 people died prematurely due to PM10 (particulate The bushmeat trade in Central Africa, and wildlife markets in Asia are examples of activities that both have impacts on the environment, and carry risk of disease emergence. In Viet Nam, the illegal trade in wildlife currently generates US$20 million/year. Wild meat is a critical source of protein and income for forest dwellers and rural poor. However, commercial demand for wild meat has been growing as a result of urban consumption, from wildlife restaurants and medicine shops, but also from markets in neighbouring countries. Rates of wildlife harvesting are unsustainable, and threaten species such as the small-toothed palm civet with extinction. In wildlife markets, mammals, birds and reptiles come in contact with dozens of other species and with countless numbers of people, increasing opportunity for disease transmission. Not surprisingly, during the 2003 Sudden Acute Respiratory Syndrome (SARS) epidemic, several of the early patients in Guangdong Province, China, worked in the sale or preparation of wildlife for food. The disease may have first spread to humans from civet cats or bats in local wildlife markets. Through human air travel, SARS quickly spread to 25 countries across five continents. With more than 700 million people travelling by air annually, disease outbreaks can easily grow into worldwide epidemics. It is estimated that every year between 1.1 and 3.4 million tonnes of undressed wild animal biomass, or bushmeat, are consumed by people living the Congo Basin. The wild meat trade, commercial hunting of wild animals for meat, has decimated endangered populations of long-lived species such as chimpanzees. Trade is global in nature, and primate meat has even been found in markets in Paris, London, Brussels, New York, Chicago, Los Angeles, Montreal and Toronto. Contact with primate blood and bodily fluids during hunting and butchering has exposed people to novel viruses. Between 2000 and 2003, 13 of 16 Ebola outbreaks in Gabon and the Republic of Congo resulted from the handling of gorilla or chimpanzee carcasses. A recent study documents simian foamy virus (SFV) and human T-lymphotic (HTLV) viruses in individuals engaged in bushmeat hunting in rural Cameroon. Box 1.4 Wild meat trade Commercial demand for wild meat has been growing and rates of wildlife harvesting are unsustainable. Credit: Lise Albrechtsen
  • 17. Box 1.5 Material well-being from fisheries ENV I RONMENT FOR DE V E LOPMENT 17 matter with a diameter less than 10 micrometers) outdoor pollution and 1.6 million due to PM10 indoor air pollution (WHO 2002) (see Chapter 2). Chapter 4 highlights how the overexploitation and pollution of freshwater ecosystems – rivers, lakes, wetlands and groundwater – has direct impacts on human well-being. Although access to clean water and sanitation has improved, in 2002 more than 1.1 billion people lacked access to clean water, and 2.6 billion lacked access to improved sanitation (WHO and UNICEF 2004). Annually, 1.8 million children die from diarrhoea, making the disease the world’s second biggest killer of children (UNDP 2006). Many heavy metals, such as mercury and lead, are found in water and sediments, and are a major concern as they can accumulate in the tissues of humans and other organisms (UNESCO 2006). Numerous activities contribute to heavy metal contamination. Burning coal, incineration, urban and agricultural run-off, industrial discharges, small-scale industrial activities, mining, and landfill leakages are among the main ones described in Chapters 2, 3 and 4. Changes in the environment have also resulted in the emergence of diseases. Since 1980, more than 35 infectious diseases have emerged or taken on new importance. These include previously unknown, emerging diseases, such as HIV, SARS and avian influenza (H5N1), as well as diseases once thought controllable, such as dengue fever, malaria and bubonic plague (Karesh and others 2005, UNEP 2005a). Human-induced changes to the environment, such as climate change, land use change and interaction with wildlife (see Box 1.4), have driven this recent epidemiological transition (McMichael 2001, McMichael 2004). Growing human contact with wildlife, caused by population pressure on remaining relatively undisturbed environmental resources, increases the opportunity for pathogen exchange (Wolfe and others 1998). Globalization, in turn, has an effect on disease emergence as disease agents have the opportunity to move into new niches, and meet new, vulnerable populations. A recent UNEP report on Avian Influenza and the Environment states: “If the transfer of Asian lineage H5N1 between domestic flocks and wild birds is to be reduced, it will become essential to take measures to minimize their contact. Restoring wetland health will reduce the need for migrating wild birds to share habitat with domestic poultry” (UNEP 2006). Material needs People depend on natural resources for their basic needs, such as food, energy, water and housing. In many communities, particularly in developing countries, environmental resources, including fisheries, timber, non-timber forest products and wildlife, directly contribute to income and other material assets required to achieve a life that one values. The ability to meet material needs is strongly linked to the provisioning, regulating and supporting services of ecosystems (MA 2003). More than 1.3 billion people depend on fisheries, forests and agriculture for employment – close to half of all jobs worldwide (see Box 1.5) (FAO 2004a). In Asia and the Pacific, small-scale fisheries contributed 25 per cent to the total fisheries production of Malaysia, the Philippines, and Thailand for the decade ending in 1997 (Kura and others 2004). In Africa, more than 7 in 10 people live in rural areas, with most engaged in resource-dependent activities (IFAD 2001). The corresponding small-scale production accounts for a significant percentage of the GDP in many African countries (IFPRI 2004). Moreover, small-scale agriculture accounts for more than 90 per cent of Africa’s agricultural production (Spencer 2001). A study of households in the Masvingo province in southeast Zimbabwe indicates that 51 per cent of incomes are from agriculture, and that the total income from the environment averages 66 per cent (Campbell and others 2002). Where resources are degraded, livelihoods are placed at risk. Forest loss may reduce The fisheries sector plays an important role in material well-being, providing income generation, poverty alleviation and food security in many parts of the world. Fish is an important protein source, especially in the developing world, providing more than 2.6 billion people with at least 20 per cent of their average per capita animal protein intake. The world’s population growth outpaced that of total fish supply and FAO projections indicate that a global shortage is expected (see Chapter 4). While fish consumption increased in some regions, such as South East Asia, Europe and North America, it declined in others, including sub-Saharan Africa and Eastern Europe. The collapse of the Canadian east coast cod fishery in the late 1980s had devastating impacts on local fishing communities, and illustrates that developed countries are not immune to the economic implications of mismanaging natural resources. It resulted in unemployment for 25 000 fishers and 10 000 other workers (see Box 5.2 and Figure 7.17 in Chapters 5 and 7 respectively). Sources: Delgado and others 2003, FAO 2004b, Matthews 1995
  • 18. the availability of food, energy resources and other forest products, which, in many communities, support trade and income earning opportunities. Increasing evidence shows that investment in ecosystem conservation, such as watershed management, results in increased income for the rural poor. In the Adgaon watershed in India, the annual days of employment (wage labour) per worker increased from 75 days before watershed rehabilitation to 200 days after restoration was completed (Kerr and others 2002). In Fiji, strengthening the traditional “no-take” management system to promote recovery of marine life has resulted in a 35–43 per cent increase in income over a period of three years (see Box 7.13) (WRI 2005). In a pioneering people-led watershed management project in India, the implementation of a participatory restoration scheme led to halving the distance to the water table, a doubling of land under irrigation, and an increase in the total agricultural income of the village from about US$55 000 in 1996, before watershed regeneration, to about US$235 000 in 2001 (D’Souza and Lobo 2004, WRI 2005). Security Security incorporates economic, political, cultural, social and environmental aspects (Dabelko and others 2000). It includes freedom from threats of bodily harm, and from violence, crime and war. It means South Pacific Western Indian Ocean millions 1.8 1.4 1.0 18 SECTION A: OVERVIEW having stable and reliable access to resources, the ability to be secure from natural and human disasters, and the ability to mitigate and respond to shocks and stresses. Environmental resources are a critical part of the livelihoods of millions of people, and when these resources are threatened through environmental change, people’s security is also threatened. “At the centre of sustainable development is the delicate balance between human security and the environment” (CHS 2006). The Earth has shown clear signs of warming over the past century. Eleven of the last 12 years (1995–2006) rank among the 12 warmest years in the instrumental record of global surface temperature (since 1850) (IPCC 2007). As Chapter 2 describes, climate change is very likely to affect ecological regulating services, resulting in increased frequency and intensity of extreme weather hazards in many regions around the globe (IPCC 2007), and greater insecurity for much of the world’s population (Conca and Dabelko 2002). The impacts of extreme weather events will fall disproportionately upon developing countries, such as Small Island Developing States (SIDS) (see Figure 1.2), as well as on the poor in all countries (IPCC 2007). During Hurricane Katrina in the United States in 2005, impoverished people without access to private transportation were unable Figure 1.2 Number of people affected by disasters of natural origin in SIDS Note: Excluding earthquakes, insect infections and volcanic eruptions. Source: GEO Data Portal, compiled from EM-DAT undated 2.0 0 1987 0.8 Caribbean 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2004 2002 2003 1.6 1.2 0.6 0.4 0.2 3.03 5.92
  • 19. ENV I RONMENT FOR DE V E LOPMENT 19 to leave the city. People in poor health or lacking bodily strength were less likely to survive the Indian Ocean tsunami in 2004. For example, in villages in North Aceh, Indonesia, women constituted up to 80 per cent of deaths (Oxfam 2005). In Sri Lanka, a high mortality rate was also observed among other vulnerable groups: children and the elderly (Nishikiori and others 2006). Environmental change can also affect security through changes in provisioning services, which supply food and other goods. Scarcity of shared resources has been a source of conflict and social instability (deSombre and Barkin 2002). Disputes over water quantity and quality are ongoing in many parts of the world. The apparent degradation of Easter Island’s natural resources by its Polynesian inhabitants, and the ensuing struggle between clans and chiefs, provides a graphic illustration of a society that destroyed itself by overexploiting scarce resources (Diamond 2005). Natural resources can play an important role in armed conflicts. They have often been a means of funding war (see Box 1.6). Armed conflicts have also been used as a means to gain access to resources (Le Billion 2001), and they can destroy environmental resources. Natural resources, including diamonds and timber, helped fuel civil war in Liberia and Sierra Leone during the 1990s. Diamonds were smuggled from Sierra Leone into Liberia and onto the world market. In the mid- 1990s, Liberia’s official diamond exports ranged between US$300 and US$450 million annually. These diamonds have been referred to as “blood diamonds,” as their trade helped finance rebel groups and the continued hostilities. By the end of the war in 2002, more than 50 000 people had died, 20 000 were left mutilated and three-quarters of the population had been displaced in Sierra Leone alone. As civil wars raged in Sierra Leone and Liberia, hundreds of thousands of refugees fled to safety in Guinea. In 2003, about 180 000 refugees resided in Guinea. Between Sierra Leone and Liberia, there is a small strip of land belonging to Guinea known as the “Parrot’s Beak,” because of the parrot shape contour of the international border between the countries (depicted as a black line on both images). This strip is where refugees constituted up to 80 per cent of the local population. The 1974 image shows small, evenly spread, scattered flecks of light green in the dark green forest cover of the Parrot’s Beak and surrounding forests of Liberia and Sierra Leone. These flecks are village compounds, with surrounding agricultural plots. The dark areas in the upper left of the image are most likely burn scars. In the 2002 image Parrot’s Beak is clearly visible as a more evenly spread light grey and green area surrounded by darker green forest of Liberia and Sierra Leone. The light colours show deforestation in the “safe area” where refugees had set up camp. Many of the refugees integrated into local villages, creating their own family plots by cutting more trees. As a result the isolated flecks merged into one larger area of degraded forest. The forest devastation is especially obvious in the upper left part, where areas that were green in 1974 now appear grey and brown, also due to expanded logging. Box 1.6 Conflict in Sierra Leone and Liberia, and refugee settlement in Guinea Sources: Meredith 2005, UNEP 2005b, UNHCR 2006a Credit: UNEP 2005b
  • 20. Insecurity caused by bad governance or war can contribute to environmental degradation. Security requires the current and future availability of environmental goods-and-services, through good governance, mechanisms for conflict avoidance and resolution, and for disaster prevention, preparedness and mitigation (Dabelko and others 2000, Huggins and Box 1.7 Chemicals affect Arctic peoples Ocean currents Surface water circulation River inflow Note: Rivers and ocean currents are important pathways for water-soluble contaminants and those that are attached to particles in the water. Note: Winds provide a fast route for contaminants from industrial areas to the Arctic especially in winter. 20 SECTION A: OVERVIEW others 2006, Maltais and others 2003). Inequitable governance and institutions may prevent people from having secure livelihoods, as illustrated by land tenure conflicts in Southern Africa (Katerere and Hill 2002), and by poor management in Indonesia’s peat swamps (Hecker 2005). In both examples, the resource is closely linked to local livelihoods, and insecurity is a result not so much of scarcity but of unequal access to and distribution of these vital resources. In other cases, as illustrated in Box 1.6, degradation may result from changes in settlement patterns as people are forced to flee an area due to hostilities or war. It has become clear in recent years that joint management on environmental matters is needed to facilitate cooperation across societal and international boundaries to avoid conflict (Matthew and others 2002; UNEP 2005b). The case of cooperative endeavours to deal with fisheries decline in Lake Victoria is an excellent example. Cooperation on water management and transnational ecosystems can also foster diplomatic habits of consultation and dialogue with positive political results, suggesting that human and environmental security are very closely linked (Dodds and Pippard 2005). Social relations The environment also affects social relations by providing cultural services, such as the opportunity to express aesthetic, cultural or spiritual values associated with ecosystems (MA 2005a). The natural world provides opportunities for observation and education, recreation and aesthetic enjoyment, all of which are of value to a given society. In some communities, the environment underpins the very structure of social relations. As described in Chapter 5, many cultures, particularly indigenous ones, are deeply interwoven with the local environment. Climate change is a major concern for SIDS and their high cultural diversity; SIDS are imperilled by sea-level rise and increases in the intensity and number of storms (Watson and others 1997) (see Chapter 7). Tuvalu is an example of an island vulnerable to environmental change. Even though its culture is strongly related to the local environment, the islanders may have to consider relocating to other countries to escape rising sea level as a result of climate change. Coping mechanisms embedded in such cultures might be lost, making society less resilient to future natural disasters (Pelling and Uitto 2001). As described in Chapters 5 and 6, the relationships that indigenous peoples have with the environment play an important role in their identity and overall well-being. Scientific assessments have detected persistent organic pollutants (POPs) and heavy metals in all components of the Arctic ecosystem, including in people. The majority of these substances are present in the ecosystems and diets of Arctic peoples as a result of choices (such as using the insecticide toxaphene on cotton fields) by industrial societies elsewhere. Contaminants reach the Arctic from all over the world through wind, air and water currents (see Figure 1.3), entering the food chain. Inuit populations in the eastern Canadian Arctic and Greenland have among the highest exposures to POPs and mercury from a traditional diet of populations anywhere. A sustainable lifestyle, with ancient roots in the harvesting, distribution and consumption of local renewable resources, is endangered as a result. Sources: Doubleday 1996, Van Oostdam 2005 Beaufort Gyre Transpolar Drift Wind frequencies Winter: 25% Summer: 5% Wind frequencies Winter: 15% Summer: 5% Wind frequencies Winter: 40% Summer: 10% Arctic front, summer Arctic front, winter Figure 1.3 Pollutants paths to the Arctic Credit: AMAP 2002
  • 21. Figure 1.4 Population by region 2003 ENV I RONMENT FOR DE V E LOPMENT 21 A diet of traditional foods plays a particularly important role in the social, cultural, nutritional and economic health of indigenous peoples living in the Arctic (Donaldson 2002). Hunting, fishing, and the gathering of plants and berries are associated with important traditional values and practices that are central to their identity as indigenous peoples. Their traditional food is compromised by environmental contaminants (see Box 1.7 and Figure 1.3) and climate change (see Chapter 6), and this affects all dimensions of indigenous well-being. The issue becomes magnified in light of the lack of accessible, culturally acceptable and affordable alternatives. Store food is expensive, and lacks cultural significance and meaning. Long-term solutions require that Arctic lifestyles be considered when development choices are made in industrial and agricultural regions around the world (Doubleday 2005). DRIVERS OF CHANGE AND PRESSURES Environmental changes and the effects on human well-being are induced by various drivers and pressures. Drivers such as demographic changes, economic demand and trade, science and technology, as well as institutional and socio-political frameworks induce pressures which, in turn, influence the state of the environment with impacts on the environment itself, and on society and economic activity. Most pressures on ecosystems result from, for example, changes in emissions, land use and resource extraction. Analyses of the linkages shown by the drivers-pressures-state-impacts- responses (DSPIR) framework (described in the Reader’s Guide to the report) form the foundation on which the GEO-4 assessment is constructed. In the two decades since the Brundtland Commission, these drivers and pressures have changed, often at an increasing rate. The result is that the environment has changed dramatically. No region has been spared the reality of a changing environment, and its immediate, short- and long-term impacts on human well-being. Population Population is an important driver behind environmental change, leading to increased demand for food, water and energy, and placing pressure on natural resources. Today’s population is three times larger than it was at the beginning of the 20th century. During the past 20 years global population has continued to rise, increasing from 5 billion in 1987 to 6.7 billion in 2007 (see Figure 1.4), with an average annual growth rate of 1.4 per cent. However, large differences in growth are evident across regions, with Africa billions 3.5 3.0 2.5 1.5 1.0 0.5 and West Asia recording high growth rates, and the European population stabilizing (see Chapter 6 for more detail). Although the world population is increasing, the rate of increase is slowing (see Box 1.8). Forced and economic migrations influence demographic changes and settlement patterns, particularly at the regional level. There were 190 million international migrants in 2005, compared to 111 million in 1985. About one-third of migrants in the world have moved from one developing country to another, while another third have moved from a developing country to a developed country (UN 2006). Many migrants are refugees, internally displaced or stateless persons. At the end of 2005, more than 20.8 million people were classified as “of concern” to the UN High Commission for Refugees (UNHCR 2006b). These included refugees, internally displaced and stateless persons. Worldwide refugee numbers have decreased since 2000, but there has been an upward trend in numbers of other displaced groups (UNHCR 2006b). The term ecomigrant has been used to describe anyone whose need to migrate is influenced by environmental factors (Wood 2001). It has been claimed that during the mid-1990s up to 25 million people were forced to flee as a result of environmental change, and as many as 200 million people could eventually be at risk of displacement (Myers 1997). Other analyses indicated that while the environment may play a role in forced migration, migration is usually also linked to political divisions, economic interests and ethnic rivalries (Castles 2002). A clear separation between factors is often difficult. Source: GEO Data Portal, compiled from UNPD 2007 4.0 0 1987 2007 1989 1995 2.0 1999 Africa Asia and the Pacific Europe Latin America and the Caribbean North America West Asia 1991 1993 1997 2001 2005
  • 22. Box 1.8 Demographic transition The annual global population growth rate declined from 1.7 per cent in 1987 to 1.1 per cent in 2007. Significant regional variations are analysed in chapter 6. Demographic transition, the change from high birth and death rates to low birth and death rates, can explain these changes in population. As a result of economic development, fertility rates are falling in all regions. In the period between 2000 and 2005, the world recorded a fertility rate of 2.7 children per woman, compared to a fertility rate of 5.1 children per woman 50 years before. Ultimately, fertility may even drop below 2, the replacement rate, leading to a global population decline. Some European countries are at this stage, and have ageing populations. Sources: GEO Data Portal, from UNPD 2007, UNAIDS 2006 Figure 1.5 Life expectancy by region Africa Asia and the Pacific Europe Latin America and the Caribbean North America West Asia Source: GEO Data Portal, compiled from UNPD 2007 Figure 1.6 Urban population by region, per cent of total population Source: GEO Data Portal, compiled from UNPD 2005 per cent 90 70 60 50 30 20 0 22 SECTION A: OVERVIEW 1985 40 10 Africa Asia and the Pacific Europe Latin America and the Caribbean North America West Asia 80 Improved health has led to lower mortality rates and higher life expectancies in most regions (see Figure 1.5). However, life expectancy in many parts of Africa has decreased during the last 20 years, partly as a result of the AIDS pandemic. Around the world, more than 20 million people have died since the first cases of AIDS were identified in 1981. It is estimated that 39.5 million adults and children where living with HIV in 2005, of which 24.7 million were in sub- Saharan Africa. In hardest-hit countries, the pandemic has reduced life expectancy, lessening the number of healthy agricultural workers and deepening poverty. years 80 70 60 50 40 30 20 10 0 1985–90 1990–95 1995–2000 2000–05 1990 1995 2000 2005 2010 2015 2020 2025
  • 23. ENV I RONMENT FOR DE V E LOPMENT 23 Urbanization continues around the world, particularly in developing countries, where rural migration continues to fuel urban growth (see Figure 1.6). By the end of 2007, more people will be living in cities than in rural areas for the first time in history (UN-HABITAT 2006). In North East Asia and South East Asia, the population living in urban areas increased from 28–29 per cent in 1985 to 44 per cent in 2005, and is projected to reach 59 per cent by 2025 (GEO Data Portal, from UNPD 2005). In some places, the urban area is increasing faster than the urban population, a process known as urban sprawl. For example, between 1970 and 1990, the total area of the 100 largest urban areas in the United States increased by 82 per cent. Only half of this increase was caused by population growth (Kolankiewicz and Beck 2001) (see Box 1.9). A growing number of people living in urban areas are living in slums – inadequate housing with no or few basic services (UN-HABITAT 2006). In many sub-Saharan African cities, children living in slums are more likely to die from water-borne and respiratory illnesses than rural children. For 2005, the number of slum dwellers was estimated at almost 1 billion (UN-HABITAT 2006). Migration and urbanization have complex relationships with environmental change. Natural disasters, and degradation of land and local ecosystems are among the causes of migration (Matutinovic 2006). Changing demographic patterns, caused by migration or urbanization, alter land use and demand for ecosystem services (see Box 1.9). Las Vegas, the fastest growing metropolitan area in the United States, exemplifies the problems of rampant urban sprawl. As the gaming and tourism industry blossomed, so has the city’s population. In 1985, Las Vegas was home to 557 000 people, and was the 66th largest metropolitan area in the United States. In 2004, the Las Vegas-Paradise area was ranked 32nd in size, with a permanent population nearing 1.7 million. According to one estimate, it may double by 2015. Population growth has put a strain on water supplies. Satellite imagery of Las Vegas provides a dramatic illustration of the spatial patterns and rates of change resulting from the city’s urban sprawl. The city covers the mainly green and grey areas in the centre of these images recorded in 1973 and 2000. Note the proliferation of roads and other infrastructure (the rectangular pattern of black lines) and the dramatic increase in irrigated areas. Box 1.9 Urban sprawl, Las Vegas Source: UNEP 2005b Credit: UNEP 2005b
  • 24. Figure 1.7 Gross domestic product – purchasing power parity per capita thousand US$ 35 30 25 20 15 5 Urbanization in particular can exert significant pressure on the environment (see Chapter 6). Coastal urban areas often cause offshore water pollution. Coastal populations alone are expected to reach 6 billion by 2025 (Kennish 2002). In these areas, large-scale development results in excessive nutrient inputs from municipal and industrial waste. As described in Chapter 4, eutrophication contributes to the creation of dead zones, areas of water with low or no dissolved oxygen. Fish cannot survive, and aquatic ecosystems are destroyed. Dead zones are an emerging problem in Asia, Africa and South America, but are present around the world. With Box 1.10 Debt repayments continue to be a major impediment to growth 24 SECTION A: OVERVIEW population growth, and increasing industrialization and urbanization, dead zones can only continue to expand. Properly managed, cities can also become a solution for some of the environmental pressures. They provide economies of scale, opportunities for sustainable transport and efficient energy options. Economic growth Global economic growth has been spectacular during the last two decades. Gross domestic product per capita (at purchasing power parity) increased by almost 1.7 per cent annually, but this growth was unevenly spread (see Figure 1.7). People in Africa, Eastern Europe and Central Asia, and certain areas of Latin America and the Caribbean are worse off than those in North America and Central and Western Europe. Many countries in these regions experienced no growth and some even a clear economic decline between 1987 and 2004. Especially in Africa there are large differences within the region, and even where there is growth, countries are faced with a heavy debt burden (see Box 1.10). Income in Asia and the Pacific is still well below the global average, but its growth rate was twice the global average. These sub-regional differences are highlighted in Chapter 6. Economic growth and unsustainable consumption patterns represent a growing pressure on the environment, though this pressure is often distributed unequally. Dasgupta (2002) argues that economic growth is unsustainable in poor countries, partly 40 0 1987 2004 Africa Asia and the Pacific Europe Latin America and the Caribbean North America Source: GEO Data Portal, compiled from World Bank 2006b 10 Even though Africa has only 5 per cent of the developing world’s income, it carries about two-thirds of the Global South’s debt burden – over US$300 billion. Despite extreme poverty, sub-Saharan Africa transfers US$14.5 billion a year to rich nations in external debt repayments. The average sub-Saharan African country, therefore, spends three times more on repaying debt than it does on providing basic services to its people. By the end of 2004, Africa spent about 70 per cent of its export earnings on external debt servicing. At the 2005 Gleneagles Summit, G8 countries cancelled 100 per cent of debts of a number of eligible Heavily Indebted Poor Countries to three multilateral institutions – the International Monetary Fund (IMF), International Development Association (IDA) and African Development Fund. This was a step towards relieving the burden that debt repayment places on growth and social services. As a result of debt cancellation and targeted aid increases between 2000 and 2004, 20 million more children in Africa are in school. While G8 countries reaffirmed Gleneagles commitments at the 2007 Heiligendamm Summit, their ability to fulfill these promises has been questioned. Sources: Christian Reformed Church 2005, DATA 2007, Katerere and Mohamed-Katerere 2005
  • 25. ENV I RONMENT FOR DE V E LOPMENT 25 because it is sustainable in wealthy countries. Countries that export resources are subsidizing the consumption of importing countries (Dasgupta 2002). However, consumption patterns among regions are changing with the emergence of new economies and powers such as China, India, Brazil, South Africa and Mexico. China, for example, is expected to become the world’s largest economy between 2025 and 2035. Its rapid economic development is influencing global patterns of resource production and consumption, with both environmental and geopolitical consequences (Grumbine 2007). Vehicle ownership patterns illustrate the impact of changing consumption patterns (see Chapter 2). China had some 27.5 million passenger vehicles and 79 million motorcycles in use by 2004 (CSB 1987–2004). The growing trend in vehicle ownership affects urban air quality, which has clear consequences for human health. Globalization The world’s economy has been characterized by growing globalization, which is spurring the increasing integration of the global economy through trade and financial flows, and in the integration of knowledge through the transfer of information, culture and technology (Najam and others 2007). Governance has also become globalized, with increasingly complex interstate interactions, and with a growing role for non-state actors. International companies have become influential economic actors in a global governance context traditionally dominated by nations. While states “rule the world,” corporations have publicly sought the global political stage at gatherings such as the World Economic Forum and at multilateral negotiations, such as the Multilateral Agreement on Investment (De Grauwe and Camerman 2003, Graham 2000). Advances in technology and communications, such as the Internet, have also boosted the role of individuals and organizations as key players in a globalized world (Friedman 2005). Globalization raises both fears and expectations. Some suggest that increasing interdependence is good for cooperation, peace and solving common problems (Bhagwati 2004, Birdsall and Lawrence 1999, Russett and Oneal 2001). Economic integration may offer dynamic benefits, such as higher productivity. The exchange of goods-and-services also helps the exchange of ideas and knowledge. A relatively open economy is better able to learn and adopt foreign, state-of-the-art technologies than is a relatively closed economy (Coe and Helpman 1995, Keller 2002). Others, however, view growing economic interdependence as destabilizing. They say that rapid flows of investment into and out of countries cause job losses, increase inequality, lower wages (Haass and Litan 1998) and result in harm to the environment. It is argued that globalization is exploitative, and is creating a murkier future for global cooperation and justice (Falk 2000, Korten 2001, Mittelman 2000). The environment and globalization are intrinsically linked. The globalization of trade has facilitated the spread of exotic species, including the five most important freshwater suspension feeding invaders (Dressena polymorpha, D. bugensis, Corbicula fluminea, C. fluminalis and Limoperna fortunei). The zebra mussel (Dressena polymorpha) has spread through North America during the last 20 years, resulting in significant ecological and economic impacts. Its introduction corresponds with dramatic increase in wheat shipments between the US, Canada and the former Soviet Union (Karatayev and others 2007). In a globalized world, important decisions related to environmental protection may have more to do with corporate management and market outcomes than with state-level, political factors. Countries may be reluctant to enforce strict environmental laws, fearing that companies would relocate elsewhere. However, it is often forgotten that the environment itself can have an impact on globalization. Resources fuel global economic growth and trade. Solutions to environmental crises, such as climate change, require coordinated global action and greater globalization of governance (Najam and others 2007). Trade World trade has continued to grow over the past 20 years, as a result of lower transport and communication costs, trade liberalization and multilateral trade agreements, such as the North American Free Trade Agreement. Between 1990 and 2003, trade in goods increased from 32.5 to 41.5 per cent of world GDP. Differences exist between regions. In North East Asia, trade in goods increased from 47 to 70.5 per cent of GDP, and high technology exports increased from 16 to 33 per cent of manufactured exports. By contrast, trade in goods in West Asia and Northern Africa
  • 26. only increased from 46.6 per cent to 50.4 per cent of GDP. High technology exports only accounted for 2 per cent of manufactured exports in 2002 (World Bank 2005). Since 1990, least developed countries (LDC) have increased their share of world merchandise trade, but still accounted for only 0.6 per cent of world exports and 0.8 per cent of world imports in 2004 (WTO 2006). As with globalization, a two-way relationship exists between the environment and trade. Transport has increased as a result of increasing flows of goods and global production networks. Transport is now one of the most dynamic sectors in a modern economy, and has strong environmental impacts (Button and Nijkamp 2004) (see Chapters 2 and 6). Trade itself can exert pressures on the environment. Increases in international Source: UNEP 2005b 26 SECTION A: OVERVIEW grain prices may increase the profitability of agriculture, and result in the expansion of farming into forested areas in Latin America and the Caribbean, for example (see Box 1.11). The wildlife trade in Mongolia, valued at US$100 million annually, is contributing to the rapid decline of species such as saiga antelope (World Bank and WCS 2006). In the presence of market or intervention failures, international trade may also exacerbate environmental problems indirectly. For example, production subsidies in the fishing sector can promote overfishing (OECD 1994). Natural disasters, in turn, can have an impact on trade at the national level, when exports fall as a result of physical damage. One example of this linkage is the hurricane damage to oil refineries in the Gulf of Mexico in 2005. Oil production in the Gulf of Mexico, which supplies 2 per cent of the world’s crude In recent years, Chile has been considered one of the most economically competitive countries in Latin America and the Caribbean. Rapid growth in Chile’s production and export of forest products is based on the expansion and management of exotic species in newly planted forests over the past 30 years. To do so, the traditional land-use practices in small-scale logging of native forests, livestock raising and agricultural cultivation have been replaced by large-scale timber production. Many endangered tree and shrub species have been affected by this growth of planted forest, which has also led to a dramatic reduction of landscape diversity as well as goods-and-services from forests. The two images, taken in 1975 (left) and 2001 (right), show clear reductions in forested land on the one hand (red arrows), and new forest areas on the other (yellow arrows). Box 1.11 Trade, growth and the environment Credit: UNEP 2005b
  • 27. ENV I RONMENT FOR DE V E LOPMENT 27 oil, slowed following Hurricane Katrina, and crude oil prices jumped to over US$70 a barrel (WTO 2006). Trade may also be positive for the environment. Debate rages over whether or not free trade will raise incomes to a point where environmental protection becomes a priority (Gallagher 2004). At the 2002 WSSD in Johannesburg, commitments were made to expand markets for environmental goods-and-services. Liberalization of trade in goods that protect the environment may help spur the creation of industry dedicated to environmental improvements (OECD 2005). Consumer preferences can influence production standards, which can be used to improve environmental conditions. In 2006, a large grain distributor imposed a moratorium on the purchase of soy produced on deforested areas of the Amazon, as a result of a Greenpeace campaign in Europe (Cargill 2006, Greenpeace 2006). Energy The world is facing twin threats: inadequate and insecure supplies of energy at affordable prices, and environmental damage due to overconsumption of energy (IEA 2006a). Global demand for energy keeps growing, placing an ever-increasing burden on natural resources and the environment. For about three decades, world primary energy demand grew by 2.1 per cent annually, rising from 5 566 million tonnes oil equivalent (Mtoe) in 1971 to 11 204 Mtoe in 2004 (IEA 2006b). Over two-thirds of this increase came from developing countries, but OECD countries still account for almost 50 per cent of world energy demand. In 2004, primary energy use per capita in OECD countries was still 10 times higher than in sub-Saharan Africa. Figure 1.8 highlights primary energy supply per capita. Global increases in carbon dioxide emissions are primarily due to fossil fuel use (IPCC 2007), the fuels that met 82 per cent of the world’s energy demand in 2004. Traditional biomass (firewood and dung) remains an important energy source in developing countries, where 2.1 billion people rely on it for heating and cooking (IEA 2002). Use of cleaner energy sources, such as solar and wind power, remains minimal overall (see Figure 5.5, Chapter 5 for energy supply by source). The need to curb growth in energy demand, increase fuel kg of oil equivalent per person 8 000 7 000 6 000 4 000 3 000 2 000 supply diversity and mitigate climate destabilizing emissions is more urgent than ever (IEA 2006a). However, expansion of alternative energy sources, such as biofuels, must also be carefully planned. Brazil expects to double the production of ethanol, a “modern” biofuel, in the next two decades (Government of Brazil 2005). In order to produce enough crops to reach production targets, the cultivated area is increasing rapidly. The growth of farming jeopardizes entire ecoregions, like the Cerrado, one of the world’s biodiversity hot spots (Klink and Machado 2005). Global demand for energy keeps growing, placing an ever-increasing burden on natural resources and the environment. Credit: Ngoma Photos Figure 1.8 Primary energy supply per capita Source: GEO Data Portal, from IEA 2006a 9 000 0 1987 2004 1989 1995 2003 5 000 1999 Africa Asia and the Pacific Europe Latin America and the Caribbean North America West Asia 1991 1993 1997 2001 1 000
  • 28. Technological innovation Advances in agriculture, energy, medicine and manufacturing have offered hope for continued human development and a cleaner environment. New farming technologies and practices related to water use, fertilizer and plant breeding have transformed agriculture, increasing food production and addressing undernutrition and chronic famine in some regions. Since 1970, food consumption is increasing in all regions, and is expected to continue to increase as a result of economic development and population growth. Concerns have been raised over the ability to meet future demand: 11 per cent of the world’s land is already used for agriculture, and in many places little room exists for agricultural expansion due to land or water shortages. Biotechnology, including genetic modification, as well as nanotechnology, has the potential to increase production in agriculture and contribute to advances human health (UNDP 2004), but remains subject to much controversy over effects on health and the environment. Earlier lessons from new technologies show the importance of applying the precautionary approach (CIEL 1991), because unintended effects of technological advances can lead to the degradation of ecosystem services. For example, eutrophication of freshwater systems and hypoxia in coastal marine ecosystems result from excess application of inorganic fertilizers. Advances Number of subscribers 500 300 200 100 28 SECTION A: OVERVIEW in fishing technologies have contributed significantly to the depletion of marine fish stocks. Communications and cultural patterns have also been revolutionized in the last 20 years, with the exponential growth of the Internet and telecommunications (see Figure 1.9). Worldwide, mobile phone subscribers increased from 2 per 1 000 people in 1990 to 220 per 1 000 in 2003 and worldwide Internet use increased from 1 in 1 000 in 1990 to 114 per 1 000 in 2003 (GEO Data Portal, from ITU 2005). Many developed countries lead the way in the number of Internet users, hosts and secure servers, prompting some to claim that there is a digital divide between different regions of the world. In Australia and New Zealand, for example, only 4 per cent of the population used Internet in 1996, but by 2003, that had risen to 56 per cent of the population By contrast in 2003, in poor countries such as Bangladesh, Burundi, Ethiopia, Myanmar and Tajikistan only 1 or 2 people per 1 000 used the Internet (GEO Data Portal, from ITU 2005). Governance The global and regional political context has changed considerably since the Brundtland Commission, with the end of the Cold War triggering renewed optimism in multilateral and Figure 1.9 (a) Mobile phones, per 1 000 people and (b) Internet users, per 100 people, by region Source: GEO Data Portal, compiled from ITU 2005 600 0 1990 2003 1995 2002 400 1999 Africa Asia and the Pacific Europe Latin America and the Caribbean North America West Asia 1991 1993 1997 2001 a 1992 1994 1996 1998 2000 Number of users 60 50 30 20 10 0 1990 2003 1995 2002 40 1999 1991 1993 1997 2001 b 1992 1994 1996 1998 2000
  • 29. ENV I RONMENT FOR DE V E LOPMENT 29 global governance. The 1990s was a decade of global summits on a diversity of issues, including children (1990), sustainable development (1992), human rights (1994), population (1994), social development (1995), gender equality (1995) and human settlements (1996). The new millennium has been equally active and agenda-setting, starting with the Millennium Summit in 2000, and its follow-up in 2005. Normative declarations and ambitious action plans from all these summits illustrate an emerging unity in how governments and the international community understand complex and global problems and formulate appropriate responses. The establishment of the World Trade Organization in 1994 strengthened global governance through its considerable authority in the areas of trade, while the establishment of the International Criminal Court of Justice in 2002 attempted to do the same for crimes against humanity. Some important reforms have happened within the UN system, including an approach that increasingly uses partnerships (such as the Global Water Partnership) and institutionalized processes to strengthen the participation of civil society (such as the UNEP’s Global Civil Society Forum and Global Women’s Assembly on Environment). At the regional level, countries have expanded or established institutions to enhance cooperation, including the European Union (EU), the North American Free Trade Agreement (NAFTA), the Southern Common Market (MERCOSUR), the Association of Southeast Asian Nations (ASEAN) and the African Union (AU). Regions became more visible in global deliberations, through, for example, the emphasis on regional preparation meetings for the World Summit on Sustainable Development. The national level remains central in governance, despite discussions in the context of globalization and regionalization. Some countries are adopting innovative governance systems and there has been a trend towards both political and fiscal decentralization of governance to sub-national levels. This does not necessarily mean that local authorities have been empowered. It has been argued that decentralization without devolution of power can be a way to strengthen the presence of the central authority (Stohr 2001). Local governments have also engaged much more widely in international cooperation in various arenas, and their role has been strengthened at the global level through the establishment in 2000 of the UN Advisory Committee of Local Authorities (UNACLA) and the World Urban Forum in 2002, as well as the founding of the United Cities and Local Governments Organization in 2004. RESPONSES Interactions between drivers and pressures, and their consequent impacts on ecosystem services and human well-being present challenges that could not be foreseen in 1987. There is an urgent need for effective policy responses at all levels – international, regional, national and local. As highlighted in the other chapters of this report, the range and scope of response options available to policy-makers has progressively evolved over the past 20 years (see Box 1.12), with a diversity of multilateral environmental agreements and institutions now involved in trying to address the challenges. The increase in governance regimes has brought about its own challenges, including competition and overlap. An interlinkages approach is essential to managing the environment, not in its individual parts but more holistically. This approach recognizes that the environment itself is interlinked; land, water and atmosphere are connected in many ways, particularly through the carbon, nitrogen and water cycles. Chapter 8 highlights both the biophysical and governance regimes interlinkages. Chapter 10 highlights the evolution of policy response measures – from a focus on command-and- Box 1.12 Types of responses Command-and-control regulation includes standards, bans, permits and quotas, zoning, liability systems, legal redress, and flexible regulation. Direct provisions by government deal with environmental infrastructure, eco-industrial zones or parks, protected areas and recreation facilities, and ecosystem rehabilitation. Public and private sector engagement relates to public participation, decentralization, information disclosure, eco-labelling, voluntary agreements and public-private partnerships. Market use includes environmental taxes and charges, user charges, deposit-refund systems, targeted subsidies, and the removal of perverse subsidies. Market creation addresses issues of property rights, tradeable permits and rights, offset programmes, green programmes, environmental investment funds, seed funds and incentives.
  • 30. control policies to creating markets and incentives, particularly for industry to implement voluntary measures aimed at minimizing environmental damage. For conventional, well-known environmental problems with proven solutions, it is necessary to continue to apply, and to further improve upon previously successful approaches. Countries that have yet to address such problems should apply these proven, workable solutions to current problems. Previously successful approaches have generally addressed changes to pressures, for example by regulating emission levels, land use or resource extraction. In order to address less-known persistent (or emerging) problems, transformative policies are needed. These policies address the drivers of environmental problems, such as demographic change and consumption patterns. Adaptive management is essential, to enable policy-makers 30 SECTION A: OVERVIEW to learn from previous experience as well as to make use of a variety of new tools that may be needed. Economic instruments Today, greater emphasis is being placed on the potential use of economic instruments to help correct market failures. These instruments were promoted by Principle 16 of the Rio Declaration: “National authorities should endeavour to promote the internalization of environmental costs and the use of economic instruments.” Natural resources can be seen as a capital asset belonging to a general portfolio, which is comprised of other assets and capitals, including material, financial, human and social. Managing this portfolio in a good and sustainable manner to maximize its returns and benefits over time is good investment. It is also central to sustainable development. A variety of economic instruments exist, including property rights, market creation, fiscal instruments, charge systems, financial instruments, liability systems, and bonds and deposits. There is a mix of so-called market-based instruments (MBIs) and command-and-control instruments to enable policy-makers to better manage and get more accurate information regarding the portfolio of capital assets. Table 1.2 summarizes different economic instruments, and how they can be applied to different environmental sectors. One of the tools is valuation, which can be used to help better assess the value of ecosystem services, and the costs of human-induced changes to the environment. Valuation Environmental ministries and agencies are often the last to benefit from investments, because economics and growth generation take precedence in government spending decisions. This is often due to lack of information on the value and carrying limits of the Earth’s ecosystems. Measurement of economic development and progress has often been linked to measures of economic output such as Gross National Product (GNP). Such aggregate measurements do not consider the depletion of natural capital caused by the consumption and production of goods-and-services. National accounting systems need revision to better include the value of the changes in the environmental resource base due to human activities (Mäler 1974, Dasgupta and Mäler 1999). Valuing different goods-and-services involves comparisons across different sets of things. How these things are accounted for, and how the services provided by the ecosystems, for example, improve well-being is called the accounting price. Table 1.3 illustrates different approaches to valuation, and how these approaches might be used to help assess the impact of policies on environmental change and human well-being. A “set of institutions capable of managing the natural resources, legal frameworks, collecting resource rents, redirecting these rents into profitable investments” is key to effective use of valuation (World Bank 2006a). Valuing natural resources and evaluating policies where institutions such as markets do not exist, and where there is a lack of individual property rights, pose challenges. Under such uncertainties, and where divergent sets of values exist, the economic value of common resources can be measured by the maximum amount of other goods-and-services that individuals are willing to give up to obtain a given good or service. Therefore, it is possible to weigh the benefits from an activity such as the construction of a dam against its negative impacts on fishing, livelihoods of nearby communities, and changes to scenic and aesthetic values. Box 1.13 provides an example of non-market valuation using the contingent valuation method (CVM).
  • 31. ENV I RONMENT FOR DE V E LOPMENT 31 Table 1.2 Economic instruments and applications Property rights Market creation Fiscal instruments Charge systems Financial instruments Liability systems Bonds and deposits Forests Communal rights Concession building Taxes and royalties Reforestation incentives Natural resource liability Reforestation bonds, forest management bonds Water resources Water rights Water shares Capital gains tax Water pricing Water protection charges Oceans and seas Fishing rights, Individual transferable quotas Licensing Oil spill bonds Minerals Mining rights Taxes and royalties Land reclamation bonds Wildlife Access fees Natural resource liability Biodiversity Patents Prospecting rights Transferable development rights Charges for scientific tourism Natural resource liability Water pollution Tradeable effluent permits Effluent charges Water treatment fees Low-interest loans Land and soils Land rights, use rights Property taxes, land-use taxes Soil conservation incentives (such as loans) Land reclamation bonds Air pollution Tradeable emission permits Emission charges Technology subsidies, low-interest loans Hazardous waste Collection charges Deposit refund systems Solid waste Property taxes Technology subsidies, low-interest loans Toxic chemicals Differential taxation Legal liability, liability insurance Deposit refund Climate Tradeable emission entitlements Tradeable forest protection obligations Tradeable CO2 permits Tradeable CFC quotas CFC quota auction Carbon offsets Carbon taxes BTU tax CFC replacement incentives Forest compacts Human settlements Land rights Access fees Tradeable development quotas Transferable development rights Property taxes, land-use taxes Betterment charges Development charges Land-use charges Road tolls Import fees Development completion bonds Source: Adapted from Panayotou 1994
  • 32. Valuation presents a set of challenges beyond conflicting value systems or lack of existing market institutions. It uses notional and proxy measures to estimate the economic values of tangible and intangible services provided by the environment. An increasing body of valuation work has been undertaken on provisioning services of ecosystems. It has produced estimates of the value of non-timber forest products, forestry, and the health impacts of air pollution and water-borne diseases. However, studies on less tangible but yet important services, such as water purification and the prevention of natural disasters, as well as recreational, aesthetic and cultural services, have been hard to get. To get objective monetary estimates of these services remains a challenge. Market data is limited to a small number 32 SECTION A: OVERVIEW of services provided by ecosystems. Furthermore, methodologies such as cost-benefit analysis and CVM may raise problems of bias. The use of market and non-market-based instruments has also shown gaps in addressing distributional and intergenerational equity issues (MA 2005b), notably with regard to poverty-related issues. Finally, many valuation studies estimating the impact of policies or projects on human well-being fail due to the lack of sufficiently precise estimates of the consequences of these policies or projects now and in the future. Despite these flaws, valuation may be a useful tool with which to examine the complex relationships and feedback involving the environment, economic growth and human well-being. Table 1.3 Purpose and application of different valuation approaches Approach Why it is done How it is done Determining the total value of the current flow of benefits from an ecosystem. To understand the contribution that ecosystems make to society and to human well-being. Identify all mutually compatible services provided. Measure the quantity of each service provided, and multiply by the value of each service. Determining the net benefits of an intervention that alters ecosystem conditions. To assess whether the intervention is worthwhile. Measure how the quantity of each service would change as a result of the intervention, as compared to their quantity without the intervention. Multiply by the marginal value of each service. Examining how the costs and benefits of an ecosystem (or an intervention) are distributed. To identify winners and losers, for ethical and practical reasons. Identify relevant stakeholder groups. Determine which specific services they use, and the value of those services to that group (or changes in values resulting from an intervention). Identifying potential financing sources for conservation. To help make ecosystem conservation financially self-sustaining. Identify groups that receive large benefit flows from which funds could be extracted, using various mechanisms. Source: Adapted from Stephano 2004 An environmental impact analysis using CVM was conducted in the 1990s to explore the removal of the Elwha and Glines dams in Washington State in the United States. These two 30- and 60-metre-high dams, respectively, are old, and block the migration of fish to 110 km of pristine water located in the Olympic National Park. The dams also harm the Lower Elwha Klallam Tribe which relies on the salmon and river for their physical, spiritual and cultural well-being. Dam removal could bring substantial fishing benefits, more than tripling the salmon populations. The cost of removing the dams, and especially the sediment build-up is estimated at about US$100–$125 million. Recreational and commercial fishing benefits resulting from dam removal would not be sufficient to cover these costs. A CVM survey was conducted and yielded a 68 per cent response in Washington State, and 55 per cent response for the rest of the United States. Willingness to pay for dam removal ranged from US$73 per household for Washington to US$68 for the rest of the United States. If every household in Washington State were to pay US$73, the cost of dam removal and river restoration could be covered. If the return stemming from Washington residents’ willingness to pay was added to the rest of the US willingness to pay (the 86 million households and their willingness to pay an average of US$68 per head) in excess of US$1 billion dollars would result. After years of negotiations it has been decided that the dams will be removed, and the Elwha Restoration Project will go forward. This is the biggest dam-removal project in history, and an event of national significance in the United States. It is expected that the two dams will be removed in stages over the course of three years, between 2009 and 2011. Box 1.13 Valuing the removal of the Elwha and Glines Dams Source: American Rivers 2006, Loomis 1997, USGS 2006
  • 33. Box 1.14 The UN Decade of Education for Sustainable Development ENV I RONMENT FOR DE V E LOPMENT 33 Non-economic instruments In addition to economic instruments, a variety of non-economic instruments have been employed to address both well-known proven and less clear emerging (or persistent) environmental problems. Today, the emerging understanding of human well-being increasingly influences our choice of instruments. Public participation Human well-being depends on the unconstrained ability of people to participate in decisions, so that they can organize society in a way that is consistent with their highest values and aspirations. In other words, public participation is not only a matter of procedural justice, but also a precondition for achieving well-being. While this is challenging, managers should involve civil society in policy interventions. The Convention on Biological Diversity offers several examples of possible stakeholder engagement in decision making. These include CBD VII/12, The Addis Ababa Guidelines on the sustainable use of the components of biodiversity; CBD VII/14 guidelines on sustainable tourism development; and the CBD VII/16 Akwe, on voluntary guidelines for the conduct of cultural, environmental and social impact assessments for development proposals on sacred sites, lands and waters traditionally occupied or used by indigenous and local communities. The development of similar agreements and protocols that enhance effective engagement of all sectors of society should be encouraged. Education Access to information and education is a basic human right, and an important aspect of human well-being. It is also an important tool for generating knowledge that links ecological analyses to societal challenges, and is critical to the decision making process. Women and marginalized communities must be ensured access to education. The United Nations launched its Decade of Education for Sustainable Development (DESD) in 2005 and designated UNESCO as lead agency for the promotion of the Decade (see Box 1.14). Justice and ethics Since the environment affects the very basis of human well-being, it is a matter of justice to consider the impacts of environmental degradation on others, and attempt to minimize harm for both current and future generations. It has been argued that a “global ethic” is required to address the problems of the 21st century (Singer 2002). The intrinsic value of species has also been recognized (IUCN and others 1991). The pursuit of some people’s opportunities and freedoms may harm or limit those of others. It is important that policy-makers consider the adverse effects their decisions have on people and the environment in other areas or regions, since such communities do not participate in local decision making. Scenario development The use of scenarios to inform policy processes is growing, providing policy-makers with opportunities to explore the likely impacts and outcomes of various policy decisions. The goal of developing scenarios “is often to support more informed and rational decision making that takes both the known and unknown into account” (MA 2005c). Their purpose is to widen perspectives and illuminate key issues that might The overall goal of the DESD is “to integrate the principles, values, and practices of sustainable development into all aspects of education and learning.” This educational effort will encourage changes in behaviour that will create a more sustainable future in terms of environmental integrity, economic viability, and a just society for present and future generations. In the long-term, education must contribute to government capacity building, so that scientific expertise can inform policy. Source: UNESCO 2007
  • 34. otherwise be missed or dismissed. Chapter 9 uses four plausible scenarios to explore the impact of different policy decisions on environmental change and future human well-being. CONCLUSION Two decades after Our Common Future emphasized the urgency of sustainable development, environmental degradation continues to threaten human well-being, endangering health, physical security, social cohesion and the ability to meet material needs. Analyses throughout GEO-4 also highlight rapidly disappearing forests, deteriorating landscapes, polluted waters and urban sprawl. The objective is not to present a dark and gloomy scenario, but an urgent call for action. While progress towards sustainable development has been made through meetings, agreements and changes in environmental governance, real change has been slow. Since 1987, changes to drivers, such as population growth, consumption patterns and energy use, have placed increasing pressure on the state of the environment. To effectively address environmental problems, policy-makers should design policies that tackle both pressures and the drivers behind them. Economic instruments such as market creation and charge systems may be used to help spur environmentally sustainable behaviour. Valuation can help policy-makers make informed decisions about the value of changes to ecosystem services. Non-economic 34 SECTION A: OVERVIEW instruments should be used to address both well-known problems with proven solutions and less clear emerging problems. This chapter has provided an overview of the challenges of the 21st century, highlighted conceptual ideas that have emerged to analyse and understand these environmental problems, and indicated options on the way forward. The following chapters highlight areas where society has contributed to environmental degradation and human vulnerability. Everyone depends on the environment. It is the foundation of all development, and provides opportunities for people and society as a whole to achieve their hopes and aspirations. Current environmental degradation undermines natural assets, and negatively affects human well-being. It is clear that a deteriorating environment is an injustice to both current and future generations. The chapters also emphasize that alternative development paths that protect the environment are available. Human ingenuity, resilience and capacity to adapt are powerful forces from which to draw to effect change. Imagine a world in which human well-being for all is secure. Every individual has access to clean air and water, ensuring improvements in global health. Global warming has been addressed, through reductions in energy use, and investment in clean technology. Assistance is offered to vulnerable communities. Species flourish as ecosystem integrity is assured. Transforming these images into reality is possible, and it is this generation’s responsibility to start doing so. Imagine a world in which human well-being for all is secure. Transforming this into reality is possible, and it is this generation’s responsibility to start doing so. Credit: T. Mohr/Still Pictures
  • 35. ENV I RONMENT FOR DE V E LOPMENT 35 References Agarwal, B. (2000). Conceptualizing Environmental Collective Action: Why Gender Matters. In Cambridge Journal of Economics 24(3):283-310 AMAP (2002). Persistent Organic Polluatants, Heavy Metals, Radioactivity, Human Health, Changing Pathways. Arctic monitoring and Assessment Programme, Oslo American Rivers (2006). Elwha River Restoration. http://www.americanrivers.org/ site/PageServer?pagename=AMR_elwharestoration (last accessed 12 June 2007) Bass, S. (2006). Making poverty reduction irreversible: development implications of the Millennium Ecosystem Assessment. IIED Environment for the MDGs’ Briefing Paper. International Institute on Environment and Development, London Bell, D., Robertson, S. and Hunter, P. (2004). Animal origins of SARS coronavirus: possible links with the international trade of small carnivores. In Philosophical Transactions of the Royal Society London 359:1107-1114 Bhagwati, J. (2004). In Defense of Globalization. Oxford University Press, Oxford Birdsall, N. and Lawrence, R. (1999). Deep Integration and Trade Agreements: Good for Developing Countries? In Grunberg, K. and Stern, M (eds.). In Global Public Goods: International Cooperation in the 21st Century. Oxford University Press, New York, NY Braidotti, R., Charkiewicz, E., Hausler, S. and Wieringa, S. (1994). Women, the Environment and Sustainable Development. Zed, London Brown, D. (1999). Making CSD Work. In Earth Negotiations Bulletin 3(2):2-6 Brown, S. (2006). The west develops a taste for bushmeat. In New Scientist 2559:8 Button, K. and Nijkamp, P. (2004). Introduction: Challenges in conducting transatlantic work on sustainable transport and the STELLA/STAR Initiative. In Transport Reviews 24 (6):635-643 Campbell, B., Jeffrey, S., Kozanayi, W., Luckert, M., Mutamba, M. and Zindi, C. (2002). Household livelihoods in semi-arid regions: options and constraints. Center for International Forestry Research, Bogor Castles, S. (2002). Environmental change and forced migration: making sense of the debate. New Issues in Refugee Research, Working Paper No. 70. United Nations High Commission for Refugees, Geneva Cargill (2006). Brazilian Soy Industry Announces Initiative Designed To Curb Soy-Related Deforestation in the Amazon. http://www.cargill.com/news/issues/ issues_soyannouncement_en.htm (last accessed 11 June 2007) Carothers, T. and Barndt, W. (2000). Civil Society. In Foreign Policy (11):18-29 China Statistical Bureau (1987-2004). China Statistical Yearbook (1987-2004). China 28 Statistics Press (in Chinese), Beijing CIEL (1991). The Precautionary Principle: A Policy for Action in the Face of Uncertainty. King’s College, London Cleaver, F. (2000). Analysing Gender Roles in Community Natural Resource Management: Negotiation, Life Courses, and Social Inclusion. In IDS Bulletin 31(2):60-67 Coe, D. T. and Helpman, E. (1995). International R&D Spillovers. NBER Working Papers 4444. National Bureau of Economic Research, Inc, Cambridge, MA Christian Reformed Church (2005). Global Debt. An OSJHA Fact Sheet. Office of Social Justice and Hunger Action http://www.crcna.org/site_uploads/uploads/factsheet_ globaldebt.doc (last accessed 21 April 2007) CHS (2006). Outline of the Report of the Commission on Human Security. Commission on Human Security http://www.humansecurity-chs.org/finalreport/Outlines/outline. pdf (last accessed 1 May 2007) Conca, K. and Dabelko, G. (2002). Environmental Peacemaking. Woodrow Wilson Center Press, Washington, DC Dabelko, D., Lonergan, S. and Matthew, R. (2000). State of the Art Review of Environmental Security and Co-operation. Organisation for Economic Cooperation and Development, Paris Dasgupta, P. (2002). Is contemporary economic development sustainable? In Ambio 31(4):269-271 Dasgupta, P. and Mäler, K.G. (1999). Net National Product, Wealth, and Social Well- Being. In Environment and Development Economics 5:69-93 DATA (2007). The DATA Report 2007: Keep the G8 Promise to Africa. Debt AIDS Trade Africa, London De Grauwe, P. and Camerman, F. (2003). Are Multinationals Really Bigger Than Nations? In World Economics 4 (2):23-37 Delgado, C., Wada, N., Rosegrant, M., Meijer, S. and Ahmed, M. (2003). Outlook for fish to 2020. In Meeting Global Demand. A 2020 Vision for Food, Agriculture, and the Environment Initiative, International Food Policy Research Institute, Washington, DC Dernbach, J. (2002). Stumbling Toward Sustainability. Environmental Law Institute, Washington, DC DeSombre, E.R. and Barkin, S. (2002). Turbot and Tempers in the North Atlantic. In Matthew, R. Halle, M. and Switzer, J (eds.). In Conserving the Peace: Resources, Livelihoods, and Security 325-360. International Institute for Sustainable Development and The World Conservation Union, Winnipeg, MB Diamond, J. (2005). Collapse: How Societies Choose to Fail or Survive. Penguin Books, London Diener, E. (2000). Subjective well-being. The science of happiness and a proposal for a national index. In The American Psychologist 55:34-43 Dodds, F. and Pippard, T. (eds.) (2005). Human and Environmental Security: An agenda for change. Earthscan, London Donaldson, S. (2002). Re-thinking the mercury contamination issue in Arctic Canada. M.A. Thesis (Unpublished). Carleton University, Ottawa, ON Doubleday, N. (1996). “Commons” concerns in search of uncommon solutions: Arctic contaminants, catalyst of change? In The Science of the Total Environment 186:169-179 Doubleday, N. (2005). Sustaining Arctic visions, values and ecosystems: writing Inuit identity, reading Inuit Art. In Williams, M. and Humphrys, G. (eds.). Cape Dorset, Nunavut’ in Presenting and Representing Environments: Cross-Cultural and Cross- Disciplinary Perspectives. Springer, Dordrecht EM-DAT (undated). Emergency Events Database: The OFDA/CRED International Disaster Database (in GEO Data Portal). Université Catholique de Louvain, Brussels Fa, J., Albrechtsen, L. and Brown. D. (2007). Bushmeat: the challenge of balancing human and wildlife needs in African moist tropical forests. In Macdonald, D. and Service, K. (eds.) Key Topics in Conservation Biology 206-221. Blackwell Publishing, Oxford Falk, R. (2000). Human rights horizons: the pursuit of justice in a globalizing world. Routledge, New York, NY FAO (2004a). The State of Food and Agriculture 2003-2004: Agriculture Biotechnology-Meeting the Needs of the Poor? Food and Agriculture Organization of the United Nations, Rome http://www.fao.org/WAICENT/FAOINFO/ECONOMIC/ESA/en/ pubs_sofa.htm (last accessed 11 June 2007) FAO (2004b). The State of the World’s Fisheries and Aquaculture 2004. Food and Agriculture Organization of the United Nations, Rome Fischetti, M. (2005). Protecting against the next Katrina: Wetlands mitigate flooding, but are they too damaged in the gulf? In Scientific American October 24 Frey, B and Stutzer, A. (2005). Beyond Outcomes: Measuring Procedual Utility. In Oxford Economic Papers 57(1):90-111 Friedman, T. (2005). The World is Flat: A Brief History of the Twenty-First Century. Farrar, Straus, and Giroux, New York, NY Gallagher, K. (2004). Free Trade and the Environment: Mexico, NAFTA and Beyond. Stanford University Press, Stanford GEF (2006). What is the GEF? The Global Environment Facility, Washington, DC http://www.gefweb.org/What_is_the_GEF/what_is_the_gef.html (last accessed 1 May 2007) GEO Data Portal. UNEP’s online core database with national, sub-regional, regional and global statistics and maps, covering environmental and socio-economic data and indicators. United Nations Environment Programme, Geneva http://www.unep.org/ geo/data or http://geodata.grid.unep.ch (last accessed 12 June 2007) Goodall, J. (2005). Introduction. In Reynolds, V. (ed.). The Chimpanzees of the Budongo Forest. Oxford University Press, Oxford Gore, A. (2006). An Inconvenient Truth: the planetary emergency of global warming and what we can do about it. Bloomsbury, London Graham, E. (2000). Fighting the Wrong Enemy: Antiglobal Activists and Multinational Enterprises. Institute of International Economics, Washington, DC Greenpeace (2006). The future of the Amazon hangs in the balance. http://www. greenpeace.org/usa/news/mcvictory (last accessed 11 June 2007) Grumbine, R. (2007). China’s emergence and the prospects for global sustainability. In BioScience 57 (3):249-255 Haass, R., and Litan, R. (1998). Globalization and Its Discontents: Navigating the Dangers of a Tangled World. In Foreign Affairs 77(3):2-6 Hecker, J.H. (2005). Promoting Environmental Security and Poverty Alleviation in the Peat Swamps of Central Kalimantan, Indonesia. Institute of Environmental Security, The Hague IEA (2002). World Energy Outlook 2003. International Energy Agency, Paris IEA (2006a). World Energy Outlook 2006. International Energy Agency, Paris IEA (2006b). Key Energy Statistics. International Energy Agency, Paris IFAD (2001). Rural Poverty Report 2001. The Challenge of Ending Rural Poverty. International Fund for Agricultural Development, Rome http://www.ifad.org/poverty/ index.htm (last accessed 1 May 2007) IFPRI (2004). Ending Hunger in Africa: Prospects for the Small Farmer. International Food Policy Research Institute, Washington, DC http://www.ifpri.org/pubs/ib/ib16. pdf (last accessed 1 May 2007) IPCC (2001). Technical Summary, Climate Change 2001: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Third Assessment Report of the Intergovernmental Panel on Climate Change. Intergovernmental Panel on Climate Change. Cambridge University Press, New York, NY IPCC (2007). Climate change 2007: The Physical Science Basis. Summary for Policymakers. Contribution of Working Group 1 to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change, Geneva ITU (2005). ITU Yearbook of Statistics. International Telecommunication Union (in GEO Data Portal). IUCN, UNEP and WWF (1991). Caring for the Earth: A Strategy for Sustainable Living. The World Conservation Union, United Nations Environment Programme and World Wide Fund for Nature, Gland Jänicke, M. and Volkery, A. (2001). Persistente Probleme des Umweltschutzes. In Natur und Kultur 2(2001):45-59 Karatayev, A., Padilla, D., Minchin, D., Boltovskoy, D. and Burlakova, L. (2007). Changes in global economies and trade: the potential spread of exotic freshwater bivalves. In Bio Invasions 9:161-180 Karesh, W., Cook, R., Bennett, E. and Newcomb, J. (2005). Wildlife Trade and Global Disease Emergence. In Emerging Infectious Diseases 11 (7):1000-1002 Katerere, Y. and Hill, R. (2002). Colonialism and inequality in Zimbabwe. In Matthew, R., Halle, M. and Switzer, J. (eds.). Conserving the Peace: Resources, Livelihoods, and Security 247-71 International Institute for Sustainable Development and The World Conservation Union, Winnipeg and Gland Katerere, Y. and Mohamed-Katerere, J. (2005). From Poverty to Prosperity: Harnessing the Wealth of Africa’s Forests. In Mery, G., Alfaro, R., Kanninen, M. and Lobovikov, M. (eds.). Forests in the Global Balance – Changing Paradigms. IUFRO World Series Vol. 17. International Union of Forest Research Organizations, Helsinki Keller, W. (2002). Trade and the Transmission of Technology. In Journal of Economic Growth 7:5-24 Kennish, M. (2002). Environmental Threats and Environmental Future of Estuaries. In Environmental Conservation 29 (1):78 – 107 Kerr J., Pangare G., and Pangare V. (2002). Watershed development projects in India: An evaluation. In Research Report of the International Food Policy Research Institute 127:1-90 Klink, C. and Machado, R. (2005). Conservation of the Brazilian Cerrado. In Conservation Biology 19 (3):707-713 Kolankiewicz, L. and Beck, R. (2001). Weighing Sprawl Factors in Large U.S. Cities, Analysis of U.S. Bureau of the Census Data on the 100 Largest Urbanized Areas of the United States. http://www.sprawlcity.org (last accessed 1 May 2007) Korten, D. (2001). When Corporations Rule the World, 2nd edition. Kumarian Press, Bloomfield Kura,Y., Revenga, C., Hoshino, E. and Mock, G. (2004). Fishing for Answers: Making Sense of the Global Fish Crisis. World Resources Institute, Washington, DC Langhelle, O. (1999). Sustainable development: exploring the ethics of Our Common Future. In International Political Science Review 20 (2):129-149 Le Billion, P. (2001). The political Ecology of war: natural resources and armed conflict. In Political Geography 20:561-584 LeRoy, E., Rouquet, P., Formenty, P., Souquière, S., Kilbourne, A., Froment, J., Bermejo, M., Smit, S., Karesh, W., Swanepoel, R., Zaki, S. and Rollin, P. (2004). Multiple Ebola virus transmission events and rapid decline of central African wildlife. In Science 303:387-390 Li, W., Shi, Z., Yu, M., Ren, W., Smith, C., Epstein, J. Wang, H. Crameri, G., Hu., Z., Zhang, H., Zhang, J., McEachern, J., Field, H., Daszak, P., Eaton, B., Zhang, S. and Wang, L. (2005). Bats are natural reservoirs of SARS-like coronavirsues. In Science 310:676-679 Loomis, J. (1997). Use of Non-Market Valuations Studies. Water Resources Management Assessments. In Water Resources Update 109:5-9 MA (2003). Ecosystems and Human Well-being; a framework for assessment. Millennium Ecosystem Assessment. Island Press, Washington, DC MA (2005a). Ecosystems and Human well-being: Biodiversity Synthesis. Millennium Ecosystem Assessment. World Resources Institute. Island Press, Washington, DC
  • 36. MA (2005b). Ecosystems and Human Well-Being. Synthesis Report. Millennium Ecosystem Assessment. Island Press, Washington, DC MA (2005c). Ecosystems and Human Well-being: Volume 2 – Scenarios. Millennium Ecosystem Assessment. Island Press, Washington, DC MacDonald, D. and Service, K (2007). Key Topics in Conservation Biology. Blackwell Publications, Oxford Mäler, K-G. (1974). Environmental Economics: A Theoretical Enquiry. John Hopkins University Press, Baltimore, MB Maltais, A., Dow, K. and Persson, A. (2003). Integrating Perspectives on Environmental Security. SEI Risk and Vulnerability Programme, Report 2003-1. Stockholm Environment Institute, Stockholm Matthews, D. (1995). Common versus open access. The collapse of Canada’s east coast fishery. In The Ecologist 25:86-96 Matthew, R., Halle, M. and Switzer, J. (eds.) (2002). Conserving the Peace: Resources, Livelihoods and Security. International Institute for Sustainable Development, Winnipeg, MB Matutinovic, I. (2006). Mass migrations, income inequality and ecosystem health in the second wave of globalization. In Ecological Economics 59:199 – 203 McMichael, A. (2001). Human culture, ecological change and infectious disease: are we experiencing history’s fourth great transition? In Ecosystem Health (7):107-115 McMichael, A. (2004). Environmental and social influences on emerging infectious disease: past, present and future. Philosophical Transactions of the Royal Society of London Biology 10:1-10 Meredith, M. (2005).The State of Africa: A history of fifty years of independence. Free Press, London Government of Brazil (2005). Diretrizes de Política de Agroenergia 2006–2011. Ministério da Agricultura, Pecuária e Abastecimento, Ministério da Ciência e Tecnologia, Ministério de Minas e Energia, Ministério do Desenvolvimento, Indústria e Comércio Exterior, Brasilia Mittelman, J. (2000). Capturing Globalization. Carfax, Abingdon Myers, N. (1997). Environmental Refugees. In Population and Environment 19(2):167-82 Najam, A., Runnalls, D. and Halle, M. (2007). Environment and Globalization: Five Propositions. International Institute for Sustainable Development, Winnipeg Nishikiori, N., Abe, T., Costa, D., Dharmaratne, S., Kunii, O. and Moji, K. (2006). Who died as a result of the tsunami? Risk factors of mortality among internally displaced persons in Sri Lanka: a retrospective cohort analysis. In BMC Public Health 6:73 OECD (2005). Trade that Benefits the Environment and Development: Opening Markets for Environmental Goods and Services. Organisation for Economic Co-operation and Development, Paris OECD (1994). The Environmental Effects of Trade. Organisation for Economic Co-operation and Development, Paris Oxfam (2005). The Tsunami’s Impact on Women. Oxfam Briefing Note. http://www. oxfam.org.uk/what_we_do/issues/conflict_disasters/bn_tsunami_women.htm (last accessed 11 June 2007) Panayotou, T. (1994). Economic Instruments for environmental Management and Sustainable Development. Environmental Economics series Paper No.1, United Nations Environment Programme, Nairobi Peiris, J., Guan, Y. and Yuen, K. (2004). Severe acute respiratory syndrome. In Nature Medicine 10 (12):S88- S97 Pelling, M. and Uitto, J. (2001). Small island developing states: natural disaster vulnerability and global change. In Environmental Hazards 3:49-62 Peterson, D. (2003). Eating Apes. University of California Press, London Prakash, A. (2000). Responsible Care: An Assessment. In Business and Society 39(2):183-209 Rahnema, M. (Ed.) (1997). The Post-Development Reader. Zed Books, London Russett, B. and Oneal, J. (2001). Triangulating Peace: Democracy, Interdependence, and International Organizations, The Norton Series in World Politics. W. W. Norton and Company, London Sen, A. (1985). Commodities and Capabilities, Oxford University Press, Oxford Sen, A. (1992). Inequality Re-examined. Clarendon Press, Oxford Sen, A. (1999). Development as Freedom. Oxford University Press, Oxford Shiva, V. (1991). The Violence of the Green Revolution: Third World Agriculture, Ecology and Politics. Zed Books, London Singer, P. (2002). One World. Yale University Press, London Smith, K. (2006). Oil from bombed plant left to spill. In Nature 442:609 36 SECTION A: OVERVIEW Solow, R. M. (1991), Sustainability: An Economist’s Perspective. The Eighteen J. Seward Johnson Lecture to the Marine Policy Center, Woods Hole Oceanographic Insitution. In Economics of the Environment: Selected Readings (ed. R. Dorfman and N.s Dorfman) 179-187. Norton, New York, NY D’Souza, M. and Lobo, C. (2004). Watershed Development, Water Management and the Millennium Development Goals. Paper presented at the Watershed Summit, Chandigarh, November 25-27, 2004. Watershed Organization Trust, Ahmednagar Spencer, D. (2001). Will They Survive? Prospects for Small farmers in sub-Saharan Africa. Paper Presented in Vision 2020: Sustainable food Security for All by 2020. International Conference Organized by the International Food Policy Research Institute (IFPRI), September 4-6, 2001, Bonn Speth, J. (2004). Red Sky at Morning: America and the Crisis of the Global Environment. Yale University Press, New Haven and London Stefano, P., Von Ritter, K. and Bishop, J. (2004). Assessing the Economic Value of Ecosystem Conservation. Environment Development Paper No.101. The World Bank, Washington, DC Stohr, W. (2001). Introduction. In New Regional Development Paradigms: Decentralization, Governance and the New Planning for Local-Level Development. (ed. Stohr, W., Edralin, J. and Mani, D). Contributions in Economic History Series (225). Published in cooperation with the United Nations and the United Nations Centre for Regional Development. Greenwood Press, Westport, CT UN (2000). United Nations Millennium Declaration. United Nations, New York, NY http://www.un.org/millennium/declaration/ares552e.htm (last accessed 1 May 2007) UN (2002). Report of the World Summit on Sustainable Development. Johannesburg, South Africa, 26 August - 4 September. A/CONF.199/20. United Nations, New York, NY UN(2004). Human Rights and Poverty Reduction. A conceptual framework. United Nations Office of the High Commissioner for Human Rights. United Nations, New York and Geneva UN (2006). Trends in Total Migrant Stock: The 2005 Revision. Population Division of the Department of Economic and Social Affairs of the United Nations Secretariat, New York, NY http://www.un.org/esa/population/publications/migration/UN_Migrant_ Stock_Documentation_2005.pdf (last accessed 1 May 2007) UNAIDS (2006). 2006 Report on Global AIDS Epidemic. United Nations Programme on HIV/AIDS, Geneva UNDP (2004). Human Development Report 2001: Making New Technologies Work for Human Development. United Nations Development Programme, New York, NY UNDP (2005a). Environmental Sustainability in 100 Millennium Development Goal Country Report. United Nations Development Programme, New York, NY UNDP (2005b) Human Development Report 2005: International Cooperation at a Crossroads. United Nations Development Programme, New York, NY UNDP (2006) Human Development Report 2006. Beyond Scarcity: power, poverty and the global water crisis. United Nations Development Programme, New York, NY UNEP (2002). Global Environment Outlook (GEO-3). United Nations Environment Programme, Nairobi UNEP (2004b). GEO Year Book 2003. United Nations Environment Programme, Nairobi UNEP (2005a). GEO yearbook 2004/2005. United Nations Environment Programme, Nairobi UNEP (2005b). One Planet Many People: Atlas of our Changing Environment. United Nations Environment Programme, Nairobi UNEP (2006). Avian Influenza and the Environment: An Ecohealth Perspective. Paper prepared by David J. Rapport on behalf of UNEP, United Nations Environment Programme and EcoHealth Consulting, Nairobi UNESCO (2007). United Nations Decade of Education for Sustainable Development (2005-2014) http://portal.unesco.org/education/en/ev.php-URL_ID=27234&URL_ DO=DO_TOPIC&URL_SECTION=201.html/ (last accessed June 25) UNESCO-WWAP (2006). Water for People. Water for Life, The United Nations World Water Development Report. United Nations Educational, Scientific and Cultural Organization, Paris and Berghahn Books, Oxford and New York, NY UN-Habitat (2006). State of the World’s Cities 2006/7. United Nations-Habitat, Nairobi UNHCR (2006a). Statistical Yearbook 2004 Country Data Sheets: Guinea. United Nations High Commission for Refugees, Geneva UNHCR (2006b). 2005 Global refugee trends statistical overview of populations of refugees, asylum-seekers, internally displaced persons, stateless persons, and other persons of concern to UNHCR. United Nations High Commission for Refugees, Geneva UNICEF (2006). Pneumonia: The forgotten killer of children. United Nations Childrens Fund and World Health Organization, New York, NY UNPD (2005). World Urbanisation Prospects: The 2005 Revision (in GEO Data Portal). UN Population Division, New York, NY http://www.un.org/esa/population/unpop. htm (last accessed 4 June 2007) UNPD (2007). World Population Prospects: The 2006 Revision (in GEO Data Portal). UN Population Division, New York, NY http://www.un.org/esa/population/unpop. htm (last accessed 4 June 2007) USGS (2006). Studying the Elwha River, Washington, in Preparation for Dam Removal. In Sound Waves Monthly Newsletter. US Geological Survey, Washington, DC http:// soundwaves.usgs.gov/2006/11/fieldwork3.html (last accessed 12 June 2007) Van Oostdam, J., Donaldson, S., Feeley, M., Arnold, D., Ayotte, P., Bondy, G., Chan, L., Dewaily, E., Furgal, C.M., Kuhnlein, H., Loring, E., Muckle, G., Myles, E., Receveur, O., Tracy, B., Gill, U., Kalhok, S. (2005). Human health implications of environmental contaminants in Arctic Canada: A review. In Science of the Total Environment 351–352:165–246 Watson, R., Zinyower, M. and Dokken, D. (eds.) (1997). The regional impacts of climate change: an assessment of vulnerability. Summary for Decision Makers. Special Report of IPCC Working Group II. Intergovernmental Panel on Climate Change WBCSD (2007). Then & Now: Celebrating the 20th Anniversary of the “Brundtland Report” – 2006 WBCSD Annual Review. World Business Council for Sustainable Development, Geneva WCED (1987). Our Common Future. Oxford University Press, Oxford WHO (2000). Guidelines for Air Quality. WHO/SDE/OEH/00.02, World Health Organization, Geneva WHO (2002) The World Health Report. Reducing risks, promoting healthy life. World Health Organization, Geneva WHO (2006). Preventing disease through healthy environments: Towards an estimate of the environmental burden of disease. World Health Organization, Geneva WHO and UNICEF (2004). Meeting the MDG drinking-water and sanitation target: A mid-term assessment of progress. World Health Organization and United Nations Children’s Fund, Geneva and New York, NY Wolfe, N., Escalante, A., Karesh, W., Kilbourn, A., Spielman, A. and Lal, A. (1998). Wild Primate Populations in Emerging Infectious Disease Research: The Missing Link? In Emerging Infectious Diseases 4 (2):148-159 Wolfe, N., Heneine, W., Carr, J., Garcia, A., Shanmugam, V., Tamoufe, U., Torimiro, J., Prosser, T., LeBreton, M., Mpoudi-Ngole, E., McCutchan, F., Birx, D., Folks, T., Burke, D. and Switzer, W. (2005). Emergence of unique primate T-lymphotropic viruses among central African bushmeat hunters. In Proceedings of the National Academy of Sciences 102 (22):7994 – 7999 Wolfe, N., Switzer. W., Carr, J., Bhullar, V., Shanmugam, V., Tamoufe, U., Prosser, A., Torimiro, J., Wright, A., Mpoudi-Ngole, E., McCutchan, F., Birx. D., Folks, T., Burke, D. and Heneine, W. (2004). Naturally acquired simian retrovirus infections in central African hunters. In The Lancet 363:932- 937 Wood, W.B. (2001). Ecomigration: Linkages between environmental change and migration. In Zolberg, A.R. and Benda, P. M.(eds.) Global Migrants, Global Refugees. Berghahn, Oxford World Bank (2005). The Little Data Book 2005. The World Bank, Washington, DC World Bank (2006a). Where is the Wealth of Nations? Measuring Capital for the 21st Century. The World Bank, Washington, DC World Bank (2006b). World Development Indicators 2006 (in GEO Data Portal). The World Bank, Washington, DC World Bank and Wildlife Conservation Society (2006). The Silent Steppe: the Illegal Wildlife Trade Crisis. The World Bank, Washington DC WTO (2006). World Trade Report 2006: Exploring the Links Between Subsidies, Trade and the WTO. World Trade Organization, Geneva WRI (2005). World Resources 2005: The Wealth of the Poor – Managing Ecosystems to Fight Poverty. World Resources Institute in collaboration with the United Nations Development Programme, the United Nations Environment Programme and The World Bank. World Resources Institute, Washington, DC