The
Evolution of Trade and Environment Linkages
Despite years of reckoning that environment and trade are
inter-related the WTO has not as yet established a mechanism
that fully addresses this issue. There are many reasons for
this situation including: the complexity of the issue itself;
the unwillingness of the WTO to engage in this work claiming
incompetence; as well as the lack of political will from both
the developing and developed countries. The following is a
brief chronology of the evolution of trade and environment
thinking outside and within the WTO.
o The Founex Report of June 1971 and the
Environmental Measures and International Trade Group (EMIT)
was the first group to consider the relationship between development
and environment under a directive by the Secretary General
of the UN Conference on Human Development(1972)
o The Stockholm Conference on Human Environment
1972 gave the matter further thought when a group produced
a report on "the Control of Industrial Pollution and
International Trade".
o The United Nations Conference on Environment
and Development (UNCED) 1992 later observed that “ an
equitable and non-discriminatory trading system had a key
contribution to make to national and international efforts
to better protect and conserve environmental resources and
promote sustainable development.” This was further reinforced
by the Rio Declaration, which cautions that environmental
standards must take account of the different environment and
development context of each nation and that there must be
“collective but differential” responsibility of
states towards environmental protection.
o The Committee on Environment and Trade
(CET) was established in 1994 at the Marrakech meeting and
was tasked with various responsibilities as detailed below:
- relating trade to environmental measures so as to promote
positive interactions to recommend changes in the multilateral
trade system in the light of the need to preserve the environment,
- to promote transparency of trade measures adopted for environmental
reasons, ensuring that they are not used for protectionist
purposes,
- to consider the linkage between the environmentally motivated
provisions of the multilateral trading system and any charges,
taxes and other requirements prescribed for the same purpose
with regard to particular products,
- to develop effective mechanisms for the settlement of disputes
between the multilateral trading system and the multilateral
environmental agreements and to
- consider any environmental measures relating to market access,
and to the export of products whose sale was prohibited in
the country of origin
Despite this worthy mandate, the CET has
not made much progress in making trade and environment mutually
supportive.
Environmental Effects of International Trade and Trade
Liberalisation
Many international discourses have argued
that trade has implicitly been the main cause of environmental
degradation for the following reasons:
• Exploitation and extraction of primary
commodities to satisfy consumer demands in the developed countries
often causes environmental degradation related to waste mismanagement
and pollution;
• Trade in Agricultural Commodities
has in some instances resulted in over-cultivation of Marginal
lands due to the cash crop syndrome. Environmentalists argue
that trade liberalisation may stimulate economic growth and
increase production levels, which in turn could lead to higher
levels of pollution and accelerated exploitation of natural
resources. By introducing subsidies, more farmers may be lured
into cash-crops, resulting in more chemicals and additional
water and fertiliser use at unsustainable levels;
• Mining can have a devastating effect
on the landscape. Large areas are often cleared for very small
volumes of mineral outputs. Most mining, forestry and tourism
development in the developing world are undertaken by multinational
companies that take advantage of a country’s lax environmental
standards;
• There has been a growing trend toward
trade in services, such as tourism. Views are often divergent
as to the impact of tourism on the natural resource sector.
It is generally agreed that there are two types of tourism:
eco-tourism and mass tourism, each with its own impacts on
the environment and on the socio-cultural aspects of the communities
affected. Mass tourism has the greatest impact on the environment
as it is likely to place excessive strain on natural resources,
due to overcrowding brought about by the high concentration
of hotels and other recreation facilities, leading in some
cases to pollution. The excessive infrastructure, may among
other things, destroy the natural resource base that attracts
tourists;
• The production or manufacture of
international products in developing countries where environmental
regulations are not yet stringent is the main cause of air
and water pollution. Production levels of export commodities
tend to match world prices and when these increase, production
levels also increase, leading to more pollution.
• Article XX of GATT allows nations
to depart from the provisions of the Agreement for purposes
of protecting the health and life of persons, animals and
plants and to conserve non-renewable natural resources. This
provision has been used mainly by developed countries to put
in place a host of environmental measures (refer to annex
1), which some argue have tended to restrict the movement
of goods, particularly from developing countries into developed
country markets.
Potential Areas of Conflict
The linkage between trade and the environment continues to
be the focus of WTO debate, which has centred around the following
issues:
• Is the relationship between multilateral
environments and the international trade system, mutually
supportive?
• Little has been done to integrate Multilateral Environmental
Agreements (MEAs), into the decisions of the trade body.
• Contradictions have been observed between TRIPs and
the Convention on Biological Diversity (CBD) (Refer to Annex
2). The CBD gives nations sovereign public rights over their
biological resources. National sovereignty implies that countries
have the right to prohibit Intellectual Property Rights (IPRs)
on life forms (biological resources). TRIPs overlooks this
right by requiring the provision of IPRs on micro-organisms,
non-biological and micro-biological process, as well as patents
and/or sui generis protection of plant varieties. (see also
SEATINI Factsheet 2)
• The environmental provisions in most
trade agreements tend to be general and non-committal, as
is the case with the North American Agreement on environmental
co-operation, which supplements the North American Free Trade
Agreement (NAFTA).
• The Trade measures imposed by MEAs,
with a view to getting compliance from non-parties, such as
required by the Montreal Protocol and CITES, are not specifically
provided for in Article XX of GATT and may actually violate
GATT provisions.
• The WTO remains uncertain on how
Article XX of GATT may be adjusted to take into account trade
related measures based on environmental agreements. The majority
of members of the Committee on Environment and Trade are of
the view that Article XX of GAAT does not permit an MEA party
to impose unilateral trade restrictions that are inconsistent
with WTO obligations.
• GATT considers subsidies to be unfavourable,
as they distort competition,. However other subsidies, especially
those that seek to promote the adaptation of environmental
requirements, are considered non-actionable which means that
no action can be taken against countries applying them. This
may be the case with subsidies imposed in line with the Climate
Change Convention, for example. In reality however, the subsidies
that have been applied by developing countries for diversifying
their productive base have been considered actionable, whilst
those by the developed countries have been considered non-actionable.
REFERENCES
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and the Environment: World Watch Institute Paper 113
Housman R (1994): Reconciling Trade and Environment:
Lessons from the North American Free Trade Agreement: Environment
and Trade 3, UNEP
Hurni H. (1996): Precious Earth: From Soil and water
Conservation to Sustainable Land Management: International
Soil Organization and Centre for Development and Environment
Konz P, Bellmann C. Assunciao L. and Melendez-Ortiz R.
(eds) 2000. “ Trade, Environment and Sustainable Development”
Views from Sub-Saharan and Latin America, A Reader: ICTSD-UNU/IAS,
Geneva, 2000
Repetto R (1994): Trade and Sustainable Development: Environment
and Trade1, UNEP
Vaugan S. (1994): Concepts and Principles of International
Environmental Law: An introduction: United nations Environment
Program : Environment and Trade 2
Diversity: Volume 11 Nos 1&2 1995: A news Journal
for the International Genetic Resources Community
Diversity: Volume 14 No1&2 1998 Ecosystems: The CBD
Framework for Action, 10th Global BiodiversityForum
ECOFORUM: Volume 21 Number 2, July 1997
WTO (1998): Trading into the Future: WTO Publications
The South Centre 1998: The WTO Multilateral Trade Agenda and
the South.
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Brown l. R., Flavin C. and French H. 2000: State of the World
2000; The WorldWatchInstitute
Annex 1: Environmental Measures and The
Implications That These Have On International Trade.
| Environmental Measure |
Implication on international trade |
| National
Product, process and production methods standards (PPMs)
Product standards relate to the quality,
performance and safety of dimensions including toxicity,
emission of pollutants etc.
Process standards regulate how good
produce must be and include issues of energy efficient
production and cleaner production, often linked to ISO
series |
Products
which do not meet the set criteria, may not be imported
into a given country.
In essence trade restrictions can
only be imposed if the product has acquired harmful
characteristics. If however the product is intact and
not harmful, But the process of production has harmed
the environment, this is considered unrelated PPM and
hence is exempt from trade restriction. |
| Eco-labelling schemes are closely related to
the PPMs, they are sponsored schemes for granting labels
to products informing that the product is environmentally
friendly or was produced in a manner that caused the
least damage to the environment |
This gives a competitive advantage
to labelled products. |
| Subsidies are
financial or other benefits conferred by a government
to domestic industries. This has caused much controversy
in the WTO particularly with respect to agricultural
subsidies conferred to farmers by the EU. |
If the subsidies are introduced in
sectors that are open to foreign trade, then the subsidy
may be discriminatory as it confers unfair advantage
to local producers, thereby having an adverse effect
on the trade interest of other members, where such subsidies
do not exist.
Subsidies may violate the “polluter
pays principle” |
| Joint Implementation agreements under the Climate Change
Convention. These in effect allow the trading of emissions
between developing and developed countries |
This raises the issue of commitment
of trade to environmental protection, since a country
can actually buy the right to emit |
| Export of Domestically prohibited
goods.
In the wake of a number of MEAs such as the Montreal
Protocol and the Convention on Persistent Organic Pollutants,
some developing countries are exporting banned substances
to members who are not party to these MEAs. |
This in essence is dumping and may
provoke countries to put in place countervailing measures. |
| Domestic environmental legislation
and standards, e.g. energy efficiency standards |
May prevent the entry into a country
of goods and services that have not been produced to
the same specifications and constitute Technical Barriers
to Trade. |
ANNEX 2: THE BIO-DIVERSITY CONVENTION
AND THE TRIPS AGREEMENT
| CBD SAYS: |
TRIPs SAYS |
THE CONFLICT |
| Nation states have sovereign public
rights over their biological resources. |
Biological resources should be subject
to private (IPRs). Compulsory licensing, in the national
interest, should be restricted. |
National sovereignty implies that
countries have the right to prohibit IPRs on life forms
(biological resources). TRIPs overlooks this right by
requiring the provision of IPRs on micro-organisms,
non-biological and micro-biological processes, as well
as patents and/or sui generis protection on plant
varieties. |
| The use or exploitation of biological
resources must give rise to equitably shared benefits |
Patents must be provided for in all
fields of technology, therefore the use or exploitation
of biological resources must be protected by IPRs. There
is no mechanism for sharing benefits between a patent
holder in one country and the donor of material in another
country from which the invention is derived. |
CBD gives developing countries a
legal basis to demand a share of benefits. Trips negate
that legal authority. |
| The use or exploitation of traditional
knowledge, innovations and practices relevant to the
use of Bio-diversity must give rise to equitably shared
benefits. |
Ditto |
CBD gives developing countries a
legal basis to demand a share of benefits. TRIPs negate
that legal authority. |
| Access to biological resources requires
the prior informed consent of the country of origin.
It also requires the ‘approval and involvement' of local
communities |
There is no provision requiring prior
informed consent for access to biological resources,
which may subsequently be protected by IPRs. |
CBD now gives states legal authority
to diminish the incidence of bio-piracy by requiring
prior informed consent. TRIPs ignores this authority
and thus promotes bio-piracy |
| States should promote the conservation
and sustainable use of Bio-diversity as a common concern
of Humankind, taking into account all rights over biological
resources. |
The safeguarding of public health
and nutrition and the public interest in general, shall
be subject to the private interest of IPR Holders as
reflected in the provisions of the TRIPs Agreement.
|
CBD places the public interest and
the common good over private property and vested interests.
TRIPs does the exact opposite. |
|