Environmental Issues
By John Vogler
Introduction
Environmental issues
on the international agenda: a brief history
The functions of
international environmental cooperation
Climate change
The environment and
International Relations theory
Conclusion
Reader's Guide
As environmental problems transcend
national boundaries they come to be a feature of international politics. This
chapter indicates that environmental issues have become increasingly prominent
on the international agenda over the last fifty years, assisted by the effects
of globalization. It shows how this has prompted attempts to arrange
cooperation
between states, and surveys the form and
function of such activity with reference to some of the main international
environmental regimes. Because climate change has become a problem of such
enormous significance, a separate section is devoted to the efforts to create
an international climate regime. This is followed by a brief consideration of
how some of the theoretical parts of this book relate to international
environmental politics.
What are Environmental
issues?
Environmental issues are harmful effects of human activity on
the biophysical environment. Environmental protection is a practice of protecting the natural
environment on individual, organizational or governmental levels, for the
benefit of both the environment and humans.
Introduction
Although humankind as a whole now appears
to be living well above the earth’s carrying capacity, the ecological footprints
of individual states vary to an extraordinary extent. See, for example, the
unusual map of the world (Fig. 22.1), where the size of countries is
proportionate to their carbon emissions. Indeed, if everyone were to enjoy the
current lifestyle of the developed countries, more than three additional
planets would be required.
This situation is rendered all the more
unsustainable by the process of globalization, even though the precise
relationship between environmental degradation and the over-use of resources,
on the one hand, and globalization, on the other, is complex and sometimes contradictory.
Globalization has stimulated the relocation of industry, population movement
away from the land, and ever-rising levels of consumption, along with associated
emissions of effluents and waste gases. While often generating greater income
for poorer countries exporting basic goods to developed country markets,
ever-freer trade can also have adverse environmental consequences, by
disrupting local ecologies and livelihoods.
On the other hand, there is little
evidence that globalization has stimulated a ‘race to the bottom’ in environmental
standards, and it has even been argued that increasing levels of affluence have
brought about local environmental improvements, just as birth rates tend to
fall as populations become wealthier. Economists claim that globalization’s
opening up of markets can increase efficiency and reduce pollution, provided
that the environmental and social damage associated with production of a good
is properly factored into its market price. Similarly, globalization has
promoted the sharing of knowledge and the influential presence of non-govern-
mental organizations (NGOs) in global environmental politics. Whatever the
ecological balance sheet of globalization, the resources on which human beings
depend for survival, such as fresh water, a clean atmosphere, and a stable
climate, are now under serious threat.
Global problems may need global solutions
and pose a fundamental requirement for global environmental governance, yet
local or regional action remains a vital aspect of responses to many problems;
one of the defining characteristics of environmental politics is the awareness
of such interconnections and of the need to ‘think globally—act locally’. NGOs
have been very active in this respect, as shown in Chapter 19 of this book.
Despite the global dimensions of
environmental change, an effective response still has to depend on a fragmented
international political system of over 190 sovereign states. Global
environmental governance consequently involves bringing to bear inter-state
relations, international law, and international organizations in addressing
shared environmental problems. Using the term ‘governance’—as distinct from government—
implies that regulation and control have to be exercised in the absence of
central government, delivering the kinds of service that a world government
would provide if it were to exist. You should refer to Chapter 15 for the
essential concepts employed in regime analysis, which is commonly applied in
the study of international governance.
Key Points
The current use and degradation of the
earth's resources is unsustainable and closely connected in sometimes
contradictory ways to the processes of globalization.
There are vast inequalities between rich
and poor in their use of the earth's resources and in the ecological shadow or
footprint that they impose on it.
The response at the international level is
to attempt to provide global environmental governance. In a system of sovereign
states, this involves international cooperation.
Environmental
issues on the international agenda: a brief history
Before the era of globalization there were
two traditional environmental concerns: conservation of natural resources and
the damage caused by pollution. Neither pollution nor wildlife respect
international boundaries, and action to mitigate or conserve sometimes had to
involve more than one state. There were also some (mostly unsuccessful)
attempts to regulate exploitation of maritime resources lying beyond national
jurisdiction, including several multilateral fisheries commissions and the
1946 International Convention for the Regulation of Whaling (see Box 22.1).
Post-Second World War global economic
recovery brought with it evidence of new pollution, leading to international
agreements in the 1950s and 1960s covering such matters as discharges from oil
tankers. This was, though, hardly the stuff of great power politics. Such
‘apolitical’ matters were the domain of new United Nations Specialized
Agencies, like the Food and Agriculture Organization, but were hardly central
to diplomacy at the UN General Assembly (UNGA) in New York.
However, in 1968 the UNGA agreed to
convene what became the 1972 UN Conference on the Human Environment (UNCHE) ‘to
focus governments’ attention and public opinion on the importance and urgency
of the question’. This Conference led to the creation of the United Nations
Environment Programme (UNEP) and the establishment of environment departments
by many governments. Yet it was already clear that, for the countries of the
South—constituting the majority in the UNGA—environmental questions could not
be separated from their demands for development, aid, and the restructuring of
international economic relations. This provided the political basis for the
concept
of sustainable development (see Box 22.2,
also see Ch. 20). Before this was formulated by the Brundtland Commission in
1987 (WCED 1987), the environment had been edged off the international agenda
by the global economic downturn of the 1970s and then by the onset of the
second cold war (see Ch. 4).
By that time, new forms of transnational
pollution such as ‘acid rain’ were causing concern alongside dawning
scientific realization that some environmental problems—the thinning of the
stratospheric ozone layer and the possibility of climate change—were truly global
in scale. The relaxation of East-West tension created the opportunity for a
second great UN conference in 1992. It’s title, the UN Conference on
Environment and Development (UNCED) reflected the idea of sustainable
development and an accommodation between the environmental concerns of
developed states and the economic demands of the South. The 1992 UNCED or
‘Earth Summit’ was at the time the largest international conference ever held.
It raised the profile of the environment as an international issue, while
providing a platform for both Agenda 21 and international conventions
on climate change and the preservation of biodiversity. The most serious
arguments at UNCED were over aid pledges to finance the environmental improvements
under discussion. Rio also created a process at the UN to review the
implementation of its agreements. The Commission on Sustainable Development was
to meet at intervals and there were follow-up UNGA Special Sessions and
full-scale conferences.
On UNCED’s tenth anniversary in 2002, the World Summit on Sustainable Development (WSSD) met at Johannesburg. The change of wording indicated how conceptions of environment and development had shifted since the 1970s. Now discussion was embedded in recognition of the importance of globalization and of the dire state of the African continent. The eradication of poverty was clearly emphasized, along with practical progress in providing clean water, sanitation, and agricultural improvements. One controversial element was the role to be played in such provision by private-public sector partnerships. Ten years later, and in the shadow of a major downturn in the global economy, Rio+20 met in Brazil. It attracted little public attention, but it did resolve to set ‘sustainable development goals for the future’.
On UNCED’s tenth anniversary in 2002, the World Summit on Sustainable Development (WSSD) met at Johannesburg. The change of wording indicated how conceptions of environment and development had shifted since the 1970s. Now discussion was embedded in recognition of the importance of globalization and of the dire state of the African continent. The eradication of poverty was clearly emphasized, along with practical progress in providing clean water, sanitation, and agricultural improvements. One controversial element was the role to be played in such provision by private-public sector partnerships. Ten years later, and in the shadow of a major downturn in the global economy, Rio+20 met in Brazil. It attracted little public attention, but it did resolve to set ‘sustainable development goals for the future’.
While the UN conferences marked the stages
by which the environment entered the international political mainstream, they
also reflected underlying changes in the scope and perception of environmental problems.
As scientific understanding expanded, it
was becoming a commonplace, by the 1980s, to speak in terms of global
environmental change, as most graphically represented by the discovery of the
ozone hole’ and the creeping realization that human activities might be
endangering the global climate. Alongside actual environmental degradation and
advances in scientific knowledge, the international politics of the environment
has responded
to the issue-attention cycle in developed
countries and the emergence of green political movements. They were fed by
public reactions to what was seen as the industrial destruction of nature as
exemplified by Rachel Carson’s influential book Silent Spring (1962).
There was also a long series of marine oil spills and industrial accidents,
which gave rise to popular alarm. The failure of established political parties
to embrace these issues effectively encouraged the birth of several new
high-profile NGOs—Friends of the Earth, Greenpeace, and the World Wildlife Fund
for Nature—alongside more established pressure groups such as the US Sierra
Club and the British Royal Society for the Protection of Birds. In the
developed world public attention waxed and waned, reviving in the early years
of the twenty-first century as the spectre of climate change appeared. Here, as
elsewhere, there were calls for international action and effective
environmental governance, but what exactly did this entail? The next section
attempts to answer this question by reviewing the functions of international
environmental cooperation.
Key Points
In the late nineteenth and early twentieth centuries, international
environmental politics was strictly limited, but from around 1960 its scope
expanded as environmental problems acquired a transnational and then a global
dimension.
The process was reflected in and stimulated by the three great UN conferences
of 1972, 1992, and 2002, whose most important role was to make the connection
between the international environmental and development agendas, as expressed
in the important concept of sustainable development.
International environmental politics reflected the issue-attention cycle in developed
countries and relied heavily on increasing scientific knowledge.
The functions of international
environmental cooperation
International cooperation establishes
governance regimes to regulate transboundary environmental problems and sustain
the global commons. Regimes encompass more than formal agreements between
states, although these are very important (see Ch. 15). Moreover, there are
other functions and consequences of international cooperation beyond regime
formation.
The pursuit of power, status, and wealth
is rarely absent from international deliberations. This is often neglected in
discussions of international environmental cooperation, even though many of the
great international gatherings, and even some of the more mundane ones, clearly
reflect struggles for national and organizational advantage. Organizations seek
to maintain their financial and staff resources as well as their place within
the UN system.
UNEP, for example, despite extensive
debates over granting it the higher and more autonomous status of a UN
Specialized Agency, remains a mere Programme. Some suspect that much of the
activity at international environmental meetings is simply to issue
declarations convincing domestic publics that something is being done, even if
environmental conditions continue to deteriorate.
Transboundary trade
and pollution control
When animals, fish, water, or pollution
cross national frontiers, the need for international cooperation arises; the
regulation of transboundary environmental problems is the longest-established
function of international cooperation, reflected in hundreds of multilateral,
regional, and bilateral agreements providing for joint efforts to manage
resources and control pollution. Prominent examples of multilateral
environmental agreements MEAs) include the 1979 Long-Range Transboundary Air
Pollution Convention and its various protocols and conventions governing such
things as the cross-border movement of hazardous waste and chemicals.
Controlling, taxing, and even promoting
trade has always been one of the more important functions of the state, and
trade restrictions can also be used as an instrument for nature conservation,
as in the 1973 Convention on International Trade in Endangered Species (CITES).
The use of trade penalties and restrictions by MEAs has been a vexed issue when
the objective of environmental protection has come into conflict with the rules
of the GATT/World Trade Organization (WTO) trade regime (see Box 22.3 and Ch.
11). Such a problem arose when the international community attempted to address
the controversial question of the new biotechnology and genetically modified
organisms (GMOs) by developing the 2000 Cartagena Protocol to the UN Convention
on Biodiversity. Opponents argued that measures to regulate the movement of
GMOs were an attempt to disguise protectionism rather than to safeguard the
environment and human health. Whether the WTO trade rules should take
precedence over the emerging biosafety rules was debated at length until the
parties agreed to avoid the issue by providing that the two sets of rules should
be ‘mutually supportive’. The background to such arguments is a wider debate
about the relationship between trade and the environment.
Norm creation
Over the last thirty years the development
of international environmental law and associated norms of
acceptable behaviour has been both rapid and innovative. Some are in the form of
quite technical policy concepts that have been widely disseminated and adopted
as a result of international discussion. The precautionary principle has gained
increasing but not uncritical currency. Originally coined by German
policy-makers, this principle states that where there is a likelihood of
environmental damage, banning an activity should not require full and
definitive scientific proof. (This was a critical issue in the discussions on
GMOs mentioned above.) Another norm is that governments should give ‘prior
informed consent’ to potentially damaging imports.
The UN Earth Summits were important in
establishing environmental norms. The 1972 Stockholm Conference produced its
‘Principle 21’ which combines sovereignty over national resources with state
responsibility for external pollution. This should not be confused with Agenda
21, issued by the 1992 Rio Earth Summit, a complex forty-chapter document
of some 400 pages that took two years to negotiate in UNCED’s Preparatory
Committee. Agenda 21 was frequently derided, not least because of its
non-binding character, but this internationally agreed compendium of
environmental ‘best practice’ subsequently had a wide impact and remains a
point of reference. For example, many local authorities have produced their
own ‘local Agenda 21s’. Under the Aarhus Convention (1998), member governments
agreed to guarantee to their publics a number of environmental rights,
including the right to obtain environmental information held by governments,
to participate in policy decisions, and to have access to judicial processes.
Aid and capacity building
Frequent North-South arguments since Rio
about the levels of aid and technology transfer that would allow developing
countries to achieve sustainable development have seen many disappointments
and unfulfilled pledges. In 1991, UNEP, UNDP, and the World Bank created the
Global Environmental Facility (GEF) as an international mechanism, specifically
for funding environmental projects in developing countries. Most environmental
conventions now aim at capacity building through arrangements for the transfer
of funds, technology, and expertise, because many of their member states
simply lack the resources to participate fully in international agreements.
The stratospheric ozone and climate change regimes aim to build capacity and
could not exist in their current form without providing for this function.
Scientific understanding
International environmental cooperation
relies on shared scientific understanding, as reflected in the form of some
important contemporary environmental regimes. An initial framework convention
will signal concern and establish mechanisms for developing and sharing new
scientific data, thereby providing the basis for taking action in a control
protocol. Generating and sharing scientific information has long been a
function of international cooperation in such public bodies as the World
Meteorological Organization (WMO) and myriad academic organizations such as
the International Council for the Exploration of the Seas (ICES) and the
International Union for the Conservation of Nature (IUCN). Disseminating
scientific information on an international basis makes sense, but it needs
funding from governments because, except in areas like pharmaceutical
research, the private sector has no incentive to do the work. International
environmental regimes usually have standing scientific committees and subsidiary
bodies to support their work. Perhaps the greatest international effort to
generate new and authoritative scientific knowledge has been in the area of
climate change, through the Intergovernmental Panel on Climate Change (IPCC)
(see Box 22.6).
Governing the commons
The global commons are usually understood
as areas and resources that do not fall under sovereign jurisdiction—they are
not owned by anybody. The high seas and the deep ocean floor come into this
category (beyond the 200-mile exclusive economic zone), as does Antarctica
(based on the 1959 Antarctic Treaty). Outer space is another highly important
common, its use being vital to modern telecommunications, broadcasting,
navigation, and surveillance. Finally, there is the global atmosphere.
The commons all have an environmental
dimension, as resources but also as ‘sinks’ that have been increasingly
degraded. The fish and whale stocks of the high seas have been relentlessly
over-exploited to the point where some species have been wiped out and
long-term protein sources for human beings are imperilled. The ocean environment
has been polluted by land-based effluent and oil, and other discharges from
ships. It has been a struggle to maintain the unique wilderness of the
Antarctic in the face of increasing pressure from human beings, and even outer
space now faces an environmental problem in the form of increasing amounts of
orbital debris left by decades of satellite launches. Similarly, the global
atmosphere has been degraded in a number of highly threatening ways, through
damage to the stratospheric ozone layer and, most importantly, by the enhanced
greenhouse effect now firmly associated with changes to the earth’s climate.
This is often characterized as a ‘tragedy of the commons’. Where there is
unrestricted access to a resource that is owned by no one, there will be an
incentive for individuals to grab as much as they can and, if the resource is
finite, there will come a time when it is ruined by over-exploitation as the
short-term interests of individual users overwhelm the longer-run collective
interest in sustaining the resource (see Box 22.4).
Within the jurisdiction of governments it
may be possible to solve the problem by turning the common into private
property or nationalizing it, but for the global commons such a solution is, by
definition, unavailable. Therefore the function of international cooperation in
this context is the very necessary one of providing a substitute for world
government to ensure that global commons are not misused and subject to tragic
collapse. This has been done through creating regimes for the governance of the
global commons, which have enjoyed varying degrees of effectiveness. Many of the
functions discussed above can be found in the global commons regimes, but their
central contribution is a framework of rules to ensure mutual agreement
between users about acceptable standards of behaviour and levels of
exploitation, consistent with sustaining the ecology of the commons.
Enforcement poses difficult challenges due
to the incentives for users to ‘free ride’ on these arrangements by taking more
than a fair share, or refusing to be bound by the collective arrangements. This
can potentially destroy regimes because other parties will then see no reason
to restrain themselves either. In local commons regimes, inquisitive neighbours
might deter rule-breaking, and a similar role at the international level can be
performed by NGOs. However, it is very difficult to enforce compliance with an
agreement on the part of sovereign states, even when they have undertaken to
comply—a fundamental difficulty for international law and hardly unique to environmental
regimes (see Ch. 14). Mechanisms have been developed to cope with this problem,
but how effective they, and the environmental regimes to which they apply, can
be is hard to judge, as this involves determining the extent to which
governments are in legal and technical compliance with their international
obligations. Moreover, it also involves estimating the extent to which state
behaviour has actually been changed as a result of the international regime
concerned. Naturally, the ultimate and most demanding test of the
effectiveness of global commons regimes is whether or not the resources or
ecologies concerned are sustained or even improved.
For the Antarctic, a remarkably
well-developed set of rules, designed to preserve the ecological integrity of
this last great wilderness, has been devised within the framework of the 1959
Treaty. The Antarctic regime is a rather exclusive club: the Treaty’s ‘Consultative
Parties’ include the states that had originally claimed sovereignty over parts
of the area, while new members of the club have to demonstrate their
involvement in scientific research on the frozen continent. Antarctic science
was crucial to the discovery of a problem that resulted in what is perhaps the
best example of effective international action to govern the commons. In 1985,
a British Antarctic Survey balloon provided definitive evidence of serious
thinning of the stratospheric ozone layer. A diminishing ozone layer is a
global problem par excellence, because the layer protects the earth and its
inhabitants from the damaging effects of the sun’s ultraviolet radiation. A
framework convention was signed about the issue in 1985, followed in 1987 by
the Montreal Protocol, imposing international controls over ozone-depleting
chemicals. The further evolution of the ozone layer regime offers the paramount
example of how international cooperation can achieve an effective solution to a
global environmental problem. The problem’s causes were isolated, international
support was mobilized, compensatory action was taken to ensure that developing
countries participated, and a set of rules and procedures was developed that
proved to be effective, at least in reducing the concentration of the offending
chemicals in the atmosphere, if not yet fully restoring the stratospheric ozone
layer (see Box 22.5).
Key Points
International environmental meetings serve
several political objectives alongside environmental aims.
A key function of international
cooperation is transboundary regulation, but attempts at environmental action
may conflict with the rules of the world trade regime.
International action is needed to promote
environmental norms, develop scientific understanding, and assist the
participation of developing countries.
International cooperation is necessary to
provide governance regimes for the global commons.
Climate change
Unlike the ozone layer problem, climate
change and the enhanced greenhouse effect had long been debated among
scientists, but only in the late 1980s did sufficient international consensus
emerge to stimulate action. There were still serious disagreements over the
likelihood that human-induced changes in mean temperatures were altering the
global climate system. The greenhouse effect is essential to life on earth.
Greenhouse gases (GHGs) in the atmosphere insulate the earth’s surface by
trapping solar radiation (see Fig. 22.2). Before the Industrial Revolution,
carbon dioxide concentrations in the atmosphere were around 280 parts per
million, and have since grown continuously (to a 2011 figure of 391 ppm) due to
burning of fossil fuels and reductions in some of the ‘sinks’ for carbon dioxide—notably
forests. Methane emissions have also risen with the growth of agriculture (IPCC
2007: 11).
The best predictions of the IPCC are that,
if nothing is done to curb intensive fossil fuel emissions, there will be a
likely rise in mean temperatures of the order of 2.4-6.4°C by 2099.
The exact consequences of this are
difficult to predict on the basis of current climate modelling, but sea level
rises and turbulent weather are generally expected. According to international
consensus, the avoidance of dangerous climate change requires that global mean
temperatures should not increase beyond 2°C. (Thai equates to keeping
atmospheric C02 concentrations below 550 ppm.) In the first decade
of the twenty-first century unusual weather patterns, storm events, and the melting
of polar ice sheets have added a dimension of public concern to the fears
expressed by the scientific community.
Climate change is really not a ‘normal’
international environmental problem—it threatens huge changes in living
conditions and challenges existing patterns of energy use and security. There
is almost no dimension of international relations that it does not actually or potentially
affect, and it has already become the subject of ‘high politics’, discussed at
G8 summits and in high-level meetings between political leaders, although its
urgency has been obscured by the persistent problems of the global economy.
To understand the magnitude of the climate
problem, a comparison may be drawn with the stratospheric ozone-issue
discussed in ‘The functions of international environmental cooperation’. There
are some similarities. CFCs (chlorofluorocarbons) are in themselves greenhouse
gases and the international legal texts on climate change make it clear that
controlling them is the responsibility of the Montreal Protocol. Also, the
experience with stratospheric ozone and other recent conventions has clearly
influenced efforts to build a climate change regime based on a framework
convention followed by a protocol.
The 1992 UN Framework Convention on
Climate Change (UNFCCC) envisaged the reduction of greenhouse gas emissions
and their removal by sinks, hoping that a start could be made by including a
commitment from the developed nations to cut their emissions back to 1990
levels by 2000. In a US election year this proved to be impossible, and the
parties had to be content with a non-binding declaration that an attempt would
be made. There was, however, a binding commitment for parties to draw up
national inventories of sources and sinks. As this included the developing
nations, many of whom were ill-equipped to fulfil this obligation, there was
also funding for capacity building. The Convention also locked the parties into
holding a continuing series of annual conferences—the CoPs—to consider possible
actions and review the adequacy of existing commitments, supported by regular
inter-sessional meetings of the subsidiary scientific and implementation bodies
and working groups. By the second CoP in Kyoto in 1997, the parties agreed a
‘control’ measure—the Kyoto Protocol, involving emissions reductions by
developed countries, facilitated by ‘flexibility mechanisms’ (see Box 22.7).
The problem faced by the framers of the
Kyoto Protocol was vastly more complex and demanding than that which their
counterparts at Montreal had confronted so successfully in 1987. Instead of
controlling a single set of industrial gases for which substitutes were
available, reducing greenhouse gas emissions would involve energy, transport,
and agriculture—the fundamentals of life in modern societies. Whether this
must involve real sacrifices in living standards and ‘impossible’ political
choices is a tough question for governments, although there are potential
economic benefits from cutting emissions through the development of alternative
energy technologies.
A second difference from the ozone regime
experience was that, despite the unprecedented international scientific effort
of the IPCC, there was no scientific consensus of the kind that had promoted
agreement on CFCs. Disagreements over the significance of human activities and
projections of future change have since narrowed dramatically, but there are
still those who have an interest in denying or misrepresenting the science.
Mistakes by the IPCC and its contributors have also damaged its authority.
There is a further problem in that, even though the effects of climate change
are not fully understood, there is enough evidence for some nations to calculate
that there might be benefits to them from climatic alterations. Regions of
Russia, for example, might become more temperate with rises in mean
temperature (although one could equally well argue the extremely damaging
effects of melting permafrost in Siberia). One generalization that could be
made with certainty is that it is the developing nations, with limited
infrastructure and major populations located at sea level, that are most
vulnerable. In recognition of this and on the understanding that a certain
level of warming is now inevitable, international attention has begun to shift
towards the problem of ‘adaptation to the inevitable effects of climate change
as well as ‘mitigation’ of its causes. Once again, the comparative simplicity
and uniformity of the stratospheric ozone problem is evident—the effects of
ozone depletion were spread across the globe and affected North Europeans as
well as those living in the southern hemisphere.
At the heart of the international politics
of climate change as a global environmental problem is the structural divide
between North and South (see Chs 8 and 23). For the Montreal Protocol there was
a solution available at an acceptable price, delivered through the Multilateral
Ozone Fund. Once again, climate change is different. One of the most
significant principles set out in the UNFCCC was that of ‘common but
differentiated responsibilities and respective capabilities’ (see Case Study
1). That is to say that, while climate change was the ‘common concern’ of all,
it had been produced as a consequence of the development of the old
industrialized nations and it was their responsibility to take the lead in
cutting emissions.
The achievement at Kyoto was to bind most
of developed nations to a set of varied emissions cuts. This achieved at least
part of the objectives of the European Union, but it was soon seen to be wholly
inadequate in terms of the projected scale of the global warming problem. In
return, the Europeans Union accepted the US proposal for the Kyoto mechanisms
and has since become their enthusiastic champion. When the Bush administration
renounced the Kyoto Protocol in 2001, much of the burden of ensuring that Kyoto
eventually entered into force fell upon the EU—and tested the diplomatic
capabilities of this new type of international actor and its component member
states. The EU also pioneered the world’s first international emissions trading
system, both to achieve the EU’s Kyoto target of an 8 per cent reduction in
emissions by 2012 and to encourage other countries to join the scheme.
The climate regime has been afflicted by
the ‘free rider’ problem. If some countries join together and agree to make
cuts that are costly, then others who do not can enjoy the environmental
benefits of such action without paying.
Thus, proceeding without the USA has been very difficult, not only because it
produces around one-quarter of global carbon dioxide emissions, but also
because its failure to be involved affects the willingness of others to
participate, and particularly the fast-developing economies of the South.
In 2007, at the Bali CoP, the problem of
US participation was addressed by a ‘road map’ in which parallel negotiations
were set up on the future of the Convention and the Protocol, with the USA
absent from the latter. The intention was to achieve a new agreement by the
2009 Copenhagen CoP, and the EU and other developed countries made pledges of
future emissions reductions. Hopes were raised by the arrival of President
Obama and his commitment to climate legislation in the USA, although not to the
Kyoto Protocol. The Copenhagen experience revealed the extent of international
structural change reflected in the emergence of the BASIC group of Brazil,
South Africa, China, and India as key players in climate diplomacy. They, along
with other developing countries and AOSIS (see Case Study 2), continued to
demand the retention of Kyoto and substantial development aid to assist with
mitigation and adaptation. At the same time developed countries backed away
from further commitment to Kyoto and the stalemate was reflected in a weak
‘Copenhagen Accord’, which was very far from a new comprehensive and binding
climate agreement. China and India offered more efficient use of fossil
fuels but not actual reductions in their projected emissions. Two years later,
at Durban in 2011, some progress was made with an agreement to conclude a new
climate agreement by 2015. This was achieved by the EU in collaboration with a
group of ‘progressive’ and least- developed countries and AOSIS. While the EU
would continue with a new phase of Kyoto, the other major emitters, including
the BASICs, agreed to negotiate on reducing their emissions. It appeared that
the strict division between Annex 1 countries (see Case Study 1) and the rest
had been overcome, but the relative lack of progress over twenty years of the
UNFCCC’s existence and the exigencies of the continuing global economic downturn
did not provide grounds for optimism. Meanwhile the scientific findings
continue to stress the accelerating gravity of the climate problem.
Key Points
Climate change, because of its
all-embracing nature and its roots in essential human activities, poses an
enormous challenge for international cooperation.
A limited start was made with the Kyoto
regime, but this was undermined by the absence of the USA. Although the 2009
Copenhagen Conference was a disappointment to climate activists, the 2011
Durban Platform held out the possibility that North-South differences might be
resolved in a new comprehensive climate agreement.
The
environment and international Relations theory
The neglect of environmental issues in
traditional and realist IR theorizing is exemplified in Hans J. Morgenthau’s
famous text, Politics among Nations (1955), which mentions the natural
environment only as a fixed contextual factor or a constituent of national
power.
However, over the last thirty years the
academic study of the international relations of the environment has developed
through the attempt to understand the circumstances under which effective
international cooperation, for example the ozone regime, can occur. The
preceding discussion of climate change shows that this question remains
important. Most scholars have used the concept of regime as explained in
Chapter 15. Note, for instance, how the defining characteristics of
regimes—principles, norms, rules, and decision-making procedures—can be applied
to the environmental cases mentioned in this chapter (see also Ch. 9). Those,
such as Oran Young (1994), who try to explain the record of environmental
regimes tend to adopt a liberal institutionalist stance, stressing as a key
motivating factor the joint gains arising from cooperative solutions to the
problem of providing public goods such as a clean atmosphere. One important
addition made by scholars of environmental politics to the regime literature
reflects the importance of scientific knowledge and the roles of NGOs in this
area. Whereas orthodox regime approaches assume that behaviour is based on the
pursuit of power or interest, students of international environmental
cooperation have noted the independent role played by changes in knowledge
(particularly scientific understanding). This cognitive approach is reflected
in studies of the ways in which transnationally organized groups of scientists
and policy-makers—often referred to as epistemic communities—have influenced
the development of environmental regimes (see Ch. 9) (Haas 1990).
Liberal institutionalist analysis of
regime creation makes the important, but often unspoken, assumption that the
problem to be solved is how to obtain global governance in a fragmented system
of sovereign states. Marxist and Gramscian writers (Paterson 2001; Newell
2012) would reject this formulation (see Ch. 8). For them, the state system is
part of the problem rather than the solution, and the proper object of study is
the way in which global capitalism reproduces relationships that are profoundly
damaging to the environment. The global spread of neo-liberal policies
accelerates those features of globalization—consumerism, the relocation of production to the
South, and the thoughtless squandering of resources—driving the global
ecological crisis (see Ch. 20). Proponents of this view also highlight: the
incapacity of the state to do anything other than assist these processes. It
follows that the international cooperation efforts described here at worst legitimize
this state of affairs and at best provide some marginal improvements to the
devastation wrought by global capitalism. For example, they would point to how
free market concepts are now routinely embedded in discussions of sustainable
development and how the WTO rules tend to subordinate attempts to provide
environmental regulation of GMOs. This argument is part of a broader debate
among political theorists concerning whether the state can ever be ‘greened’ (Eckersley 2004). The
opposing view would be that within any time frame that is relevant to coping
with a threat of the immediacy and magnitude of climate change, the state and
international cooperation remain the only plausible mechanisms for providing
the necessary global governance, and that we shall simply have to do the best we can
with existing state and international organizational structures (Vogler 2005).
The other theoretical connection that must
be made
is to the pre-eminent concern of orthodox IR—security (see Ch. 12). This link
can be thought of in two ways. First, it is argued that environmental change
contributes to the incidence of internal conflict and even inter-state war,
even though the causal connections are complex and involve many factors. It is
already evident that desertification and the degradation of other vital
resources are intimately bound up with cycles of poverty, destitution, and war
in Africa. However, if we consider such predicted consequences of climate change as mass migrations of
populations across international boundaries and acute scarcity of water and
other resources, the outlines of potential future conflicts come into sharper
focus (see Chs 20 and 23).
The link between environmental change and
armed conflict is essentially an extension of traditional thinking about security, defined in terms of collective
violence and attacks on the state (Homer-Dixon 1991,1994). A more intriguing
question is whether we should now redefine the idea of security to encompass
environmental threats as well as those stemming from terrorism and war (see
Ch.12). The UK Chief Scientist once did this by arguing that climate change
represented a more significant threat than terrorism (King 2004). As the
public becomes more sharply aware of the full magnitude of the climate problem,
political discourse begins to ‘securitize’ (Buzan, Waever, and de Wilde 1997)
the environment—that is, to characterize the environment as a security problem.
Because governments usually prioritize security matters, people wishing to
mobilize political attention and resources, and encourage potentially painful
societal adaptation, will be tempted to stretch established definitions of
security.
Key points
The environment has been a growth area for
IR scholars interested in identifying the conditions under which effective
international cooperation can emerge.
Scholars differ in the importance that
they attach to various kinds of explanatory factors in their analyses of
international environmental regime-building activities-crude calculations of
the power and interests of key actors such as states, cognitive factors such as
shared scientific knowledge, the impact of non-governmental actors, and even
the extent to which the system of states is itself part of the problem.
IR scholars are also interested in the
extent to which the environment in general and particular environmental
problems are now being seen as security issues in academic, political, and
popular discourse, and whether this securitization of the environment is
something to be welcomed.
Conclusion
This chapter has shown, briefly, how
environmental issues have moved from the margins to an increasingly central
place on the international agenda. Climate change is now widely perceived to be
at least the equal of any other issue and arguably the most important raced by
humankind. The rise to prominence of environmental issues is intimately
associated with globalization due to the strain that this places on the earth’s
carrying capacity in terms of consumption levels, resource depletion, and
rising greenhouse gas emissions. Globalization has also facilitated the growth
of transnational green politics and interventions by N'GOs to raise public
awareness, influence international conferences, and even monitor the implementation
of agreements by states.
At every stage, two distinctive aspects of
international environmental politics have played a central role. The first is
the complex relationship between scientific understanding of the biosphere,
politics, and policy, as exemplified by the interplay between the IPCC and the actions
of governments building the climate regime. The second is the connection
between environment md development, which has been expressed in the
shifting meanings given to the concept of
sustainable development and whose acknowledgement has been a precondition for
international action on a whole range of environmental issues. Nowhere is this
more evident than in debates about the future direction of the climate regime.
The international response to
environmental change has been in the form of attempts to arrange global environmental
governance through extensive cooperation between governments. This chapter has
attempted to provide some insight into the range and functions of such
regime-creating activities, which provide a basis on which the international
community is attempting to grapple with the climate problem. The academic
community has generally followed this enterprise by concentrating on the
question of how regimes may be formed and sustained. More critical theorists
will take a different view of the meaning of international cooperation (see
Ch. 8). Furthermore, the challenges posed to international theory by the global
environmental predicament will undoubtedly involve the need to think through
the connections between security, climate change, and globalization.
Case Study 1
Common but differentiated responsibilities?
A key
principle of the climate change regime, written into the 1992 UNFCCC, was the
notion of 'common but differentiated responsibilities and respective
capabilities'. This meant that although all nations had to accept
responsibility for the world's changing climate, it was developed (Annex 1)
nations that were immediately responsible because they had benefited from the
industrialization which was generally regarded as the source of the excess
carbon dioxide emissions that had caused mean temperature increases (refer to Fig. 22.1).
In the
1990s, the USA emitted around 25 per cent of the global total but had only 4.5
per cent of global population. Chinese figures were 14 per cent but with over
20 per cent of the world’s population, while the thirty-five least-developed
nations emitted under 1 per cent. Under the Kyoto Protocol the developed
countries were expected to make emissions cuts. However, by 2004 it was clear
that an effective post-2012 regime would have to involve the fast-growing
economies of the South because their 'respective capabilities' had changed. In
terms of current CO: emissions in 2011, six countries were
responsible for over 70 per cent of the world total: China 29 per cent, US 16
per cent, EU 11 per cent, India 6 per cent, Russia 5 per cent, and Japan 4 per
cent Finding a new basis for an equitable sharing of necessary emissions
reductions is fraught with problems: (1) Because GHGs have long and variable
atmospheric lifetimes, from thirty up to at least a hundred years, past
emissions must also be taken into account Thus developing countries can argue
that most of the allowable 'carbon space' has already been taken up by the
historic emission of the old industrialized economies and that the latter should
therefore, continue to take the lead. (2) Per capita emissions still vary
widely between Northern and Southern economies. Treating them in the same way
cannot be either just or politically acceptable. (3) A major part of current
Chinese emissions are the direct result of the transfer of production of goods
from the US and Europe. Who, therefore, bears the responsibility?
Case Study 2
The Alliance of Small Island States (AOSIS)
There
are a number of key coalitions that operate in climate diplomacy, including the
Umbrella Group of non-EU developed countries, the Environmental Integrity
Group, which includes Switzerland, South Korea, and Mexico, and the Group of
77/China, which has long attempted to represent the South in global
negotiations. Because of the widening differences between its members, the
G77/China often fractures into the BASIC countries, the fossil fuel exporters,
less-developed mainly African countries, and AOSIS. The Alliance has played a
disproportionately large role. Set up in 1990, its forty-four members may only
represent about 5 per cent of world population but they are driven by an
awareness that national survival is at stake. For members such as Nauru,
Tuvalu, or Vanuatu, the sea level rise associated with climate change threatens
inundation within the foreseeable future. AOSIS is an 'ad hoc lobby and negotiating
voice' coordinated through the UN missions of its members. It was influential
in the initial decision to set up the Kyoto Protocol and has agitated
consistently for a 1,5°C rather than a 2°C threshold plus compensatory
arrangements for loss and damage caused by climate change. After the Copenhagen
CoP in 2009 AOSIS was involved with the EU, Australia, and a range of other
progressive and less-developed countries in setting up the Cartagena Dialogue.
This provided a diplomatic basis for the Durban Platform agreed in 2011.
Box 22.1
Chronology
1946 International Convention for the
Regulation of Whaling
1956 UK Clean Air Act to combat 'smog' in
British cities
1958 International Convention for the
Prevention of Pollution of the Sea by Oil
1959 Antarctic Treaty
1962 Rachel Carson publishes Silent Spring
1967 Torrey Canyon oil tanker disaster
1969 Greenpeace founded
1971 At the Founex Meeting in Switzerland,
Southern experts formulate a link between environment and development
1972 United Nations Conference on the
Human Environment (UNCHE) in Stockholm Establishment of the United Nations
Environment Programme (UNEP)
1973 MARPOL Convention on oil pollution
from ships
Convention on International Trade in
Endangered Species (CITES)
1979 Long-Range Transboundary Air
Pollution Convention (LRTAP)
1980 Convention on the Conservation of Antarctic
Marine Living Resources
1982 UN Law of the Sea Convention (enters
into force in 1994)
1984 Bhopal chemical plant disaster
1985 Vienna Convention for the Protection
of the Ozone Layer The Antarctic 'ozone hole' confirmed
1986 Chernobyl nuclear disaster
1987 Brundtland Commission Report
Montreal Protocol on Substances that
Deplete the Ozone Layer 1988 1988 Establishment of the Intergovernmental Panel
on Climate Change (IPCC)
1989 Basel Convention on the Transboundary
Movement of Hazardous Wastes
1991 Madrid Protocol (to the Antarctic
Treaty) on Environmental Protection
1992 United Nations Conference on
Environment and Development (UNCED) held at Rio de Janeiro. Publication of the
Rio Declaration and Agenda 27.
United Nations Conventions on Climate Change (UNFCCC) and Biological Diversity
(CBD) both signed. Establishment of the Commission on Sustainable Development
(CSD).
1995 World Trade Organization (WTO)
founded
1997 Kyoto Protocol to the UNFCCC
1998 Rotterdam Convention on Hazardous
Chemicals and Pesticides
Aarhus Convention on Access to
Information, Public Participation in Decision-making and Access to Justice in
Environmental Matters
2000 Cartagena Protocol to the CBD on
Biosafety
Millennium Development Goals set out
2001 US President Bush revokes signature
of the Kyoto Protocol
2002 World Summit on Sustainable
Development (WSSD), Johannesburg; Johannesburg Plan of Implementation
2005 Entry into force of the Kyoto
Protocol and introduction of the first international emissions trading system
by the
European Union
2006 International discussions commenced
on the climate change regime after 2012
2007 Fourth Assessment Report of the IPCC;
Bali CoP produces a 'road map' for climate negotiations
2009 Copenhagen climate CoP fails to
provide a new international agreement
2010 Nagoya Protocol to the CBD on access
and benefit sharing
2011 Durban climate CoP aims to produce a
new agreement by 2015
2012 Rio+20 Conference
Box 22.2
Sustainable
development
Over fifty separate definitions of
sustainable development have been counted. Its classic statement was provided
by the A 987 Brundtiand Commission Report:
Sustainable development is development
that meets the needs of the present without compromising the ability of future
generations to meet their own needs. (Brundtland
et al. 1987:43)
Behind it lay an explicit recognition of
limitations to future growth that were social, technological, and
environmental. In addressing them, emphasis was placed on needs, and the
highest priority was given to those needs experienced by the world's poor.
Central to the concept was the idea of fairness between generations as well as
between the rich and poor currently inhabiting the planet.
By the time of the 2002 World Summit the
concept had been subtly altered:
to ensure a balance between economic
development, social development and environmental protection as interdependent
and mutually reinforcing components of sustainable development.
(UNGA,
A/57/532/add.l, 12 December 2002)
Box 22.3
Trade and the environment
The issue of the relationship between
trade and environmental degradation is much broader than disputes over the
relationship between the World Trade Organization (WTO) and particular
multilateral environmental agreements (MEAs). Globalization is partly shaped by
the efforts of the GATT/WTO to open up protected markets and expand world
trade. Many green activists argue that trade itself damages the environment by
destroying local sustainable agriculture and by encouraging the environmentally
damaging long-range transport of goods. The rearrangement of patterns of
production and consumption has indeed been one of the hallmarks of
globalization. Liberal economists and apologists for the WTO claim that if the
'externalities', such as the pollution caused, can be factored into the price
of a product, then trade can be beneficial to the environment through allowing
the most efficient allocation of resources. In this view, using trade
restrictions as a weapon to promote good environmental behaviour would be unacceptable-and,
indeed, the rules of the WTO allow only very limited restrictions to trade on
environmental grounds (GATT XXg), and certainly not on the basis of 'process
and production methods'. A number of trade dispute cases have largely
confirmed that import controls cannot be used to promote more sustainable or
ethical production abroad, including the famous 1991 GATT Tuna-Dolphin case
which upheld Mexican and EC complaints against US measures blocking imports of
tuna caught with the methods that kill dolphins as by-catch. Developing-country
governments remain resistant to green trade restrictions as a disguised form of
protection for developed world markets.
Box 22.4
The tragedy of the
commons-local and global
Many writers, including Garrett Hardin
(1968), who coined the term 'tragedy of the commons', have observed an inherent
conflict between individual and collective interest and rationality in the use
of property that is held in common. Hardin argued that individual actions in
exploiting an ‘open access' resource will often bring collective disaster as
the pasture, fish stock (common pool), or river (common sink) concerned suffers
ecological collapse through over-exploitation. Of course, no problem will be
perceived if the 'carrying capacity' of the common is sufficient for all to
take as much as they require, but this is rarely now the case due to the
intensity of modern exploitation and production practices, and recent
scientific advances have sharpened humankind's appreciation of the full extent
of the damage imposed on the earth's ecosystems. Hardin's solution to the
dilemma-enclosure of the commons through privatization or nationalization-has
only limited applicability in the case of the global commons, for two main
reasons: it is physically or politically impossible to enclose them, and there
is no central world government to regulate their use.
Box 22.5
The
Montreal Protocol and stratospheric ozone regime
The thinning of the stratospheric ozone
layer arose from a previously unsuspected source-artificial chemicals
containing fluorine, chlorine, and bromine, which were involved in chemical
reaction with ozone molecules at high altitudes. Most significant were the CFCs
(chlorofluorocarbons), which were developed in the 1920s as 'safe' inert
industrial gases and which had been blithely produced and used over the next
fifty years for a whole variety of purposes, from refrigeration to
air-conditioning and as propellants for hairspray. There was no universal
agreement on the dangers posed by these chemicals and production and use continued-except,
significantly, where the US Congress decided to ban some non-essential uses.
This meant that the US chemical industry found itself under a costly obligation
to find alternatives. As evidence on the problem began to mount, UNEP convened
an international conference in Vienna. It produced a 'framework convention'
agreeing that international action might be required and that the parties
should continue to communicate and develop and exchange scientific findings.
These proved to be very persuasive, particularly with the added public impetus
provided by the dramatic discovery of the Antarctic 'ozone hole'.
Within two years the parties agreed to a
Protocol under which the production and trading of CFCs and other
ozone-depleting substances would be progressively phased out. The developed
countries achieved this for CFCs by 1996 and Meetings of the Parties (MoP) have
continued to work on the elimination of other substances since that time. There
was some initial resistance from European chemical producers, but the US side
had a real incentive to ensure international agreement because otherwise its
chemical industry would remain at a commercial disadvantage. The other problem
faced by the negotiators involved developing countries, which themselves were
manufacturing CFC products. They were compensated by a fund, set up in 1990, to
finance the provision of alternative non-CFC technologies for the developing
world.
The damage to the ozone layer will not be
repaired until the latter part of the twenty-first century, given the long
atmospheric lifetimes of the chemicals involved. However, human behaviour has
been significantly altered to the extent that the scientific subsidiary body
of the Montreal Protocol has been able to report a measurable reduction in the
atmospheric concentration of CFCs.
Box 22.6
The Intergovernmental Panel on
Climate Change
Set up in 1988 under the auspices of the
World Meteorological Organization (WMO) and UNEP, the Intergovernmental Panel
on Climate Charge (IPCC) brings together the majority of the world's climate
change scientists in three working groups: on climate science, impacts, and
economic and social dimensions. They have produced assessment reports in 1990,
1995, and 2001, which are regarded as the authoritative scientific statements
on climate change. The reports are carefully and cautiously drafted with the
involvement of government representatives, and represent a consensus view.
The Fourth Assessment Report, published in
February 2007, concluded that 'warming of the climate system is unequivocal,
as is now evident from observations of increases in global average air and
ocean temperatures, widespread melting of snow and ice and rising global sea
level’ (IPCC 2007: 4). Most of the temperature increase 'is very likely due to
the observed increase in anthropogenic greenhouse gas concentrations' PCC 2007:
8, original italics). The Fifth IPCC report will be completed in 2013-14.
Box 22.7
The Kyoto Protocol
The 1997 Kyoto Protocol to the UN
Framework Convention on Climate Change committed the developed countries to
make an average of a 5.2 per cent cut in their greenhouse gas emissions from a
1990 baseline by 2012. Within this, different national targets were negotiated:
for example, 7 per cent for the USA and 8 per cent for the European Union (EU).
This was to be achieved by emissions trading (the EU set up its own system in
2005) and by complex offsetting arrangements-Joint Implementation and the Clean
Development Mechanism (CDM). Unfortunately, by 2012, the only major signatory
still committed to the Protocol and its extension was the EU.
Questions
What are the possible connections, both
negative and positive, between globalization and environmental change?
Why did environmental issues appear on the
international agenda and what were the key turning points?
How would you interpret the meaning of
sustainable development?
How can regime concepts be applied to the
study of international environmental cooperation (also see Ch. 15)?
Can international trade and environmental
protection ever be compatible?
Why did the framework convention/control
protocol prove useful in the cases of stratospheric ozone depletion and climate
change?
How does the 'tragedy of the commons'
analogy help to illustrate the need for governance of the global commons?
Describe the 'free rider' problem in
relation to the climate change regime.
Can 'common but differentiated
responsibilities' continue to be relevant to the future climate change regime?
Consider the possible security
implications of the climate predictions made by IPCC.
Further Reading
Barnett, J. (2001), The
Meaning of Environmental Security: Ecological Politics and Policy in the New
Security Era (London: Zed Books). This lively and critical book is
for readers who wish to explore the growing connections between environmental
and security issues.
Barry, J., and Eckersley, R. (eds) (2005), The
State and the Global Ecological Crisis (Cambridge, MA: MIT Press). A
provocative set of essays on the continuing relevance of the state, long
forsaken by green activists, but still the fundamental unit of global
environmental governance.
Birnie, P., and Boyle, A. (2002), International
Law and the Environment (Oxford: Oxford University Press). An
invaluable source of detailed information on formal aspects of international
environmental cooperation.
Brenton, T. (1994), The
Greening of Machiavelli: The Evolution of International Environmental Politics
(London: Earthscan). A diplomatic participant's account of the international
politics of the environment up to and including the Rio Earth Summit.
Dauvergne, P. (ed.) (2012), Handbook
of Global Environmental Politics: Second Edition
(Cheltenham: Edward Elgar). This very
extensive collection of thirty essays covering states' governance and security,
capitalism, trade and corporations, civil societies, knowledge, and ethics will
provide the reader with a more 'advanced' view of current concerns and
controversies in the field.
de Sombre, B. (2006), Global
Environmental Institutions (Abingdon: Routledge). Provides a concise
introduction within a series on global governance.
Elliott, L. (2004), The
Global Politics of the Environment (Basingstoke: Palgrave). This
comprehensive and up-to-date text provides
detailed and wide-ranging coverage of the field and of the key international
agreements.
Rutting, G. (ed.) (2011), Global Environmental Politics: Concepts, Theories
and Case Studies (Abingdon and New York: Routledge). This collection
pursues many of the themes in this chapter in greater depth.
Newell, P. (2012), Globalization and the Environment: Capitalism,
Ecology and Power (Cambridge: Polity Press). Examines the
relationship between globalization and the environment from a historical
materialist and political ecology viewpoint.
O’Neill, K. (2009), The Environment and International Relations
(Cambridge: Cambridge
University Press). An excellent and
comprehensive review of the theoretical literature in the field.
Vogler, J. (2000), The Global Commons: Environmental and
Technological Governance (Chichester: John Wiley). Uses regime
analysis to compare and account for the various international arrangements for
the ocean, Antarctic, space, and atmospheric commons.
Visit the Online Resource Centre that
accompanies this book to access more learning resources on this chapter topic
at www.oxfordtextbooks.co.uk/orc/baylis6exe/
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