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International Environmental Law Part 2 pdf
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Historical Evolution 37
• reducing by 2015 the mortality rates for infants and children under five by twothirds and maternal mortality by three-quarters, using as a baseline the 2000
mortality rate;181
• reducing the HIV/AIDs infection among young people aged fifteen to twentyfour by 25 percent in most affected countries by 2005, and globally by 2010, and
supporting a global fund to fight AIDs, malaria and tuberculosis;182
• ensuring that by 2015 all children will be able to complete a full course of primary
schooling;183
• developing integrated water resources and water efficiency plans by 2005184
(including the support of water allocation based on human needs, para. 25 (c));
• encouraging by 2010 the application of the ecosystem approach to the management of the oceans;185
• maintaining or restoring fish stocks to levels that produce maximum sustainable
yield by 2015;186
• achieving significant reduction of the current loss of biological diversity by
2010;187
• encouraging the adoption of a harmonized system for the classification and labeling of chemicals by 2008;188
• aiming to achieve by 2020 the use and production of chemicals that led to the
minimization of adverse effects on human health and the environment.189
The Implementation Plan refers to the TRIPs (Trade-Related Intellectual Property
Rights) agreement, which was adopted as a subsidiary agreement to the treaty that
established the WTO. The controversy that surrounded the TRIPs agreement is
analyzed in more detail in Chapter 9. The TRIPs agreement was viewed by many
in the developing world as an agreement designed to protect the interests of large
pharmaceutical corporations residing in the North at the expense of the health
of people in the developing world. The Implementation Plan, therefore, provides
specifically that
the TRIPs Agreement does not and should not prevent WTO members from taking
measures to protect public health. Accordingly, while reiterating our commitment to
the TRIPs Agreement, we reaffirm that the Agreement can and should be interpreted
in a manner supportive of WTO’s members’ right to protect public health and in
particular to promote access to medicines for all.190
Overall, the social and economic provisions included in the Implementation Plan
overwhelm the strictly environmental provisions. Reading through the Plan, one
181 Para. 46(f), id.
182 Para. 48, id.
183 Para. 109(a), id.
184 Para. 25, id.
185 Para. 29(d), id.
186 Para. 30(a), id.
187 Para. 42, id.
188 Para. 22(c), id.
189 Para. 22(a), id.
190 Para. 94, id.
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38 Introduction to International Environmental Law
gets the impression of going through an economic and social declaration rather than
a stricto sensu plan of environmental implementation.
During the WSSD, certain partnerships were fostered among NGOs. According
to some commentators, the WSSD strengthened the commitment of states to provide
financial sources for the cause of sustainable development.191
4.4. From Stockholm to Johannesburg
The Stockholm Conference, and ensuing environmental legislation, was one of
the first attempts to deal with environmental problems at a global scale. The result
was a number of instruments that did not offer clear standards but, nevertheless,
helped create state consensus that some environmental problems need to be tackled
internationally.
The Rio Conference was a first attempt to deal with the complexity that many
environmental problems present. The conventions that followed the Rio Conference are decidedly more elaborate instruments than those that preceded it. The
Rio Conference created an impetus to include clear and enforceable standards in
international instruments that states would be held accountable to implement. The
instruments adopted after the Rio Conference present more resemblance to the
command-and-control legislation of many developed countries.
The Rio Conference was significant because it was an attempt to find a common
ground between what developed states wanted to accomplish and what developing
countries stood for. Concepts such as sustainable development and common but
differentiated responsibilities sounded initially like principles deprived of concrete
content. In the aftermath of the conference, they have acquired strength and have
defined many subsequent international and local developments. Today, the concept
of sustainable development with its three pillars articulates successfully some of the
conditions of sustainable growth. The social and economic pillars are as important
as the environmental pillar. The concept has had an effect even on localities within
developed countries with the enunciation of the concept of “sustainable communities.”192 The principle of common but differentiated responsibilities has found
articulation in the climate change and ozone regimes through the provision of payments to developing countries in order to induce their compliance with international
agreements. Overall, the Rio Conference provided an opportunity for developing
countries to use the environmental agenda as a means to advance their concerns
about development and growth.
191 During the WSSD, a number of countries made commitments for the furtherance of the goals of the
summit. An agreement was made, for instance, to replenish the GEF with the amount of $3 billion.
The UN received thirty-two partnership initiatives with $100 million in resources for biodiversity and
ecosystem management, twenty-one partnerships for water and sanitation with at least $20 million
in resources, and thirty-two partnerships for energy projects with $26 million in resources. The EU
announced that it would increase its development assistance by more than 9 billion annually from
2006 onward. The United States announced $970 million in investments over the next three years for
water and sanitation projects and Japan announced 250 billion donation for education over a five-year
period.
192 The concept of sustainable communities has been applied in some communities in the United States,
see infra note 275.
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The WSSD promoted issues of social and economic development with a new sense
of urgency. The conference has more to do with ensuring that countries accomplish
a level of development than with providing for new environmental standards. Putting
issues of development at the core of what was initially conceived as an environmental
summit demonstrates the difficulty involved in isolating environmental concerns
from the pursuit of growth. The WSSD has posed the question of the purpose of
environmental protection in a world where many people are suffering still from
poverty and disease. It is question worth asking.
4.5. Case Law
The development of international environmental law has been influenced by the
decisions of the International Court of Justice and other tribunals that have tried to
apply in practice the principles of international law.
The Corfu Channel case was brought before the ICJ by the United Kingdom in the
aftermath of World War II.193 The case concerned the damage to ships and injuries
to officers of the British navy by a minefield located in the Corfu Strait, allegedly
planted by Albania. The United Kingdom claimed that the Albanian government
knew about the minefield and failed to notify the British ships that were passing
through the strait, exercising their right to innocent passage. The British government
further claimed that the Albanian government should be required to make reparations
because it breached its international obligation of notification. Albania, by contrast,
claimed that it knew nothing about the minefield.
The Court concluded that the fact that the minefield had been recently laid and
the fact that Albania had kept close watch on its territorial waters, during the time
the minefield was set, rendered Albania’s lack of knowledge improbable. The Court
took into account, as additional evidence of Albania’s knowledge, what happened
after the minefield explosion – namely, that the Greek authorities had appointed
a committee to inquire into the event whereas the Albanian government had not
done so. The Court found that the Albanian government should have notified the
British warships of the existence of the minefield. The Court mentioned that such
an obligation was not necessarily based on an international treaty but:
on certain general and well-recognized principles, namely: elementary considerations
of humanity, even more exacting in peace than war; the principles of the freedom
of maritime communication; and every State’s obligation not to allow knowingly its
territory to be used for acts contrary to the rights of other States.194
The pronouncement of the Court of every state’s obligation not to allow its territory
to be used for acts contrary to the rights of other states has been repeated frequently
in cases of polluting/hazardous activities that may have adverse affects on the territory of another state. Such obligation implies a duty of a polluting state to notify
other states for acts that it knows happen within its territory and can adversely affect
other states. The duty of notification, which has been repeated in many international
193 Corfu Channel Case, (UK v. Albania), April 9, 1949, (1949) ICJ Reports 4.
194 Id. at 22.
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40 Introduction to International Environmental Law
environmental instruments,195 was initially articulated in the Corfu Channel case. It
must be noted also that the Court referred to “elementary considerations of humanity” that made the conduct of Albania unlawful. Thus, humanity considerations, no
matter how imprecise they sound, become a criterion for judging the behavior of
states.
Another case with a clearer environmental focus is the Trail Smelter case.196 This
case involved a dispute between the United States and Canada regarding the damage
to United States territory inflicted by sulphur dioxide emissions from a smelting plant
at the Consolidated Mining and Smelting Company of Canada at Trail, located in
the British Columbia. In 1935, Canada and the United States agreed to submit the
dispute to arbitration.
The tribunal concluded, after examining domestic and international law, that:
under the principles of international law . . . no State has the right to use or permit the
use of its territory in such a manner as to cause injury by fumes in or to the territory of
another or the properties or persons therein, when the case is of serious consequence
and the injury is established by clear and convincing evidence.197
This conclusion of the tribunal has been cited frequently in international environmental law writings as evidence of the establishment of the concept of state liability
for environmental harm. However, it must be noted that the tribunal carefully stated
that state liability applies only when “the case is of serious consequence” and that
additionally the injury must be established “by clear and convincing evidence.”198
Furthermore, in the Trial Smelter case, Canada had in some way acquiesced to pay
some damages by virtue of the fact that it had paid damages before 1932 and had
agreed to put the issue to arbitration.199
The tribunal recognized the payment of damages for concrete cases of environmental harm but was not receptive of general claims for damage to the environment.
The tribunal recognized damages for cleared and uncleared land using the standard
established by the U.S. courts in cases of nuisance and trespass – that is, the amount
of reduction in “value of use or rental value” of the land caused by the fumes.200
The market value of the land was the criterion that was used, therefore, to establish
the amount of damages and not some sort of evaluation of natural resources damage.
The tribunal did not award damages for pastured lands, damage to livestock, and
property damage in the town of Northport. The tribunal did not award damages to
business enterprises.201 The tribunal concluded that some of these damages were too
remote and uncertain and that the parties failed to provide proof. The tribunal did
195 See Chapter 3, Section 2.2. 196 Trail Smelter Case, (United States v. Canada), April 16, 1931, March 11, 1941, 3 UN Reports of
International Arbitral Awards 1905 (1941).
197 Id. at 1907.
198 See also William A. Nitze, Acid Rain: A United States Policy Perspective, in International Law and
Pollution 329, 338 (Daniel Barstow Magraw, ed., 1991).
199 Samuel Bleicher, An Overview of International Environmental Regulation, 2 Ecology Law Quarterly
1, 22 (1972).
200 Trial Smelter case, supra note 196, at 1907.
201 Id.
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not award any damages for the injurious effects of the disposal of waste slag in the
Columbia river, thus rejecting explicitly, a claim for pure environmental damages.202
Although the tribunal was conservative in the award of damages, it played a more
decisive regulatory role. The tribunal ordered Canada to establish controls on the
emissions of sulphur dioxide by providing for maximum permissible sulfur emissions
including detailed requirements for hourly emissions.
The Trail Smelter case has launched a discourse in international law about whether
a standard of state responsibility or strict state liability has been established for polluting activities. If such a standard has been established the question is what the
prerequisites are for the success of a claim of strict liability in international incidents
of pollution. As analyzed earlier, the tribunal required that the polluting acts must
be “of serious consequence” and that the injury must be established by clear and
convincing evidence. These requirements set a high threshold for the establishment
of a standard of state liability. Policy makers must clarify two points:
• The polluting activities must be “of serious consequence.” Because some form
of pollution is part of everyday life, the amount and nature of pollution that is
significant for the establishment of a strict liability claim under international law
must be clearly established.
• There must be clear and convincing evidence of harm. This is a difficult requirement to meet, as the Trail Smelter case itself demonstrates. Most of the damage to
environment is hard to establish, as the scientific evidence is often inconclusive.
The Lac Lanoux case203 involved a decision taken by France (an upstream state) to
build a barrage on the Carol River for the purposes of hydroelectricity production.
France intended to divert the waters of the Carol River before returning them to
Spain, where they would be used for agricultural irrigation. Spain claimed that the
diversion of waters by France was against its interests, despite the eventual restitution
of waters to their original destination. Because the restitution of waters was dependent on the will of France, Spain claimed that one party was preponderant in water
management. Such preponderance was against the equality of the parties established
in the water treaties that had been signed between the parties.204
The tribunal held that although France is entitled to exercise its rights, it cannot
ignore Spanish interests. Spain is entitled to demand that its rights are respected and
that its interests are taken into consideration.205 But the tribunal held that taking
into account Spain’s interests does not mean that France must seek an agreement
with Spain before constructing works on shared river resources. The tribunal held
that subjecting a state’s right to use its watercourses to the completion of a prior
agreement with another state would give that other state essentially “a right to veto”
202 For an extensive analysis of the Trial Smelter case, see Edith Brown Weiss et al., International Environmental Law and Policy 245–62 (1998).
203 Lac Lanoux Arbitration, (France v. Spain), Nov. 16. 1957, 12 UN Reports of International Arbitral
Awards 281 (1957).
204 The three treaties at Bayonne on Dec. 1, 1856, April 14, 1862, May 26, 1866. According to Spain, the
French scheme establishes “a preponderance which is repugnant to the spirit of equality which inspires
[the treaty between the parties].” See Lac Lanoux case, pleadings of Spain, id.
205 Para. 24, id.