IPEN BRIEFING PAPER: THE POPS CONVENTION & THE TRADE RULES Prepared by Claudia Saladin, Center for International Environmental Law (USA), Morag Simpson, Council of Canadians (Canada), and Mariann Lloyd-Smith, National Toxics Network (Australia) This paper looks at issues in the POPs convention relating to potential conflicts between the POPs Convention and the rules of the World Trade Organization (WTO). Concerns over this conflict are evident in two places in the current draft of the POPs Convention the nature of the obligations contained in article D; and the inclusion of a “WTO Supremacy Clause” in article N bis of the draft Convention. This brief is premised on the principle that POPs negotiators – who include public health, environment and trade experts – are in the best position to determine the appropriate mix of measures – trade and non-trade – for dealing with POPs. Moreover, it is premised on the belief that POPs negotiators have an obligation to ensure that the best mix of available measures are authorized by the POPs Convention to deal with the health hazards that exposure to POPs pose to human and animal populations. POPs negotiators have an obligation to ensure that the best mix of available measures are authorized by the POPs Convention to deal with the health hazards that exposure to POPs pose to human and animal populations Trade measures have been an important part of many multilateral environmental agreements (MEAs). While uncertainty about the relationship between MEAs and the WTO rules is used by countries to chill the development of effective MEAs, the WTO rules themselves acknowledge that countries may take measures to protect human, animal and plant life and health, even when those measures might otherwise violate core obligations of the international trade rules. Moreover, the WTO rules acknowledge the importance of internationally agreed environmental standards. Trade measures in the POPs Convention should be considered international standards within the meaning of the WTO rules and should be deemed necessary to protect human, animal and plant life and health, as permitted in the WTO rules. For these reasons: trade-related measures can and should be included in article D and the WTO supremacy clause contained in article Nbis should be deleted. TRADE MEASURES IN MULTILATERAL ENVIRONMENTAL AGREEMENTS Multilateral environmental agreements (MEAs) are the preferred way to deal with shared global environmental problems Over 20 MEAs include trade measures as part of the toolkit of measures to address global environmental threats Uncertainty about the relationship between MEAs and the WTO trade rules is used by some countries to “chill” the development of effective new MEAs 1 Multilateral environmental agreements (MEAs) are agreements between governments to cooperatively address shared environmental problems, such as POPs. The international community prefers multilateral approaches because measures taken multilaterally are thought to be more likely motivated by a desire to solve the environmental problem at hand and less likely to be motivated by protectionism. Moreover, multilateralism provides greater assurance that the environmental problem being addressed has been acknowledged as a priority by a wide range of countries. Finally, measures developed in an international negotiating forum are more likely to be designed to equitably achieve environmental goals, taking into account the priorities and needs of both developed and developing countries. Any trade-related measure in the POPs Convention will be developed in a multilateral forum where many different countries – developing and developed, producing and consuming, large and small, rich and poor – are represented. Trade measures are now used in over 20 MEAs,1 including a number of the most important ones: The Montreal Protocol on Ozone Depleting Substances includes trade measures both between parties, and among parties and non-parties. These measures have contributed to the Protocol’s effectiveness by encouraging compliance, increasing membership and preventing increased production by non-parties. These trade measures, many of which could contravene core WTO obligations, have enabled the Protocol to reverse the trend of erosion of stratospheric ozone levels. The Convention on International Trade in Endangered Species (CITES) uses trade measures to reduce threats to endangered plant and animal species posed by the international trade in such species. The Basel Convention on the Transboundary Movement of Hazardous Waste uses trade measures to address health and environmental threats posed by the transboundary movement of hazardous wastes. The Rotterdam Convention on Prior Informed Consent allows countries to refuse consent to import certain chemicals and imposes labeling requirements on certain chemicals. Despite the importance of trade measures in MEAs, uncertainty about their relationship to the WTO rules remains. This uncertainty is used to “chill” the development of effective new MEAs by countries that see weak MEAs as in their economic interest. These countries use uncertainty about WTO rules during environmental negotiations to protect or promote their trade interests by reducing the scope of MEAs and weakening their provisions. They also use this uncertainty to argue for the insertion of “WTO supremacy clauses”, which are designed to subordinate MEA rules to those of the WTO: an approach that both fails to adequately address the underlying uncertainties, and that threatens to increase friction between the WTO and international environmental law. THE RELATIONSHIP BETWEEN THE WTO RULES AND TRADE MEASURES IN MEAS The WTO rules are contained in a number of individual agreements which together comprise the WTO Agreement. The most important of these agreements for the POPs Convention are: the General Agreement on Tariffs and Trade (GATT), which establishes the core obligations of the international trading system; the Agreement on Sanitary and Phytosanitary Measures (SPS Agreement), which applies to sanitary and phytosanitary measures (SPS measures), which are regulations aimed at 2 protecting human, animal and plant health from risks due to contaminants and toxins found in food or feedstuffs; and the Agreement on Technical Barriers to Trade (TBT Agreement), which applies to regulations regarding product specifications, labeling, packaging and other “technical” issues. The GATT contains three core obligations that are incorporated in some way in most of the individual agreements comprising the WTO Agreement. These core obligations are: The most favored nation (MFN) obligation prohibits a WTO Member State from treating the products of one trading partner differently from those of another. The national treatment obligation prohibits a WTO Member State from treating the products of is trading partners differently from domestically produced goods. The prohibition on quantitative restrictions requires WTO Members to remove non-tariff restrictions on imports, such as bans, quotas, and licenses. Its aim is to limit import barriers as much as possible to one kind of measure – tariffs – which can be progressively reduced. In cases where a measure violates any of these core obligation, it will still be considered WTO consistent if it qualifies for protection under the exceptions included in Article XX of the GATT, which includes measures “necessary for the protection of human, animal or plant life or health” (Article XX(b)). A country’s right to use these exceptions is qualified by introductory language in Article XX (the chapeau), which provides that a measure must not be applied in a way that constitutes “arbitrary or unjustifiable discrimination” between countries, or a disguised restriction on international trade. Trade measures that violate a core GATT obligation are still WTO consistent if they meet the requirements of the GATT’s environmental exceptions The relationship between the environmental exceptions and trade-related measures in MEAs is not entirely clear. However, many countries and commentators have argued that trade measures in MEAs should presumptively qualify for protection under the environmental exceptions to the GATT.2 MEAs reflect a range of perspectives, including those of large and small, rich and poor, and importing and exporting countries. Measures developed through such multilateral processes are unlikely to be motivated by protectionist intentions and will be carefully crafted to meet the goals of the MEA. The acceptance of an MEA by a wide range of parties also ensures that any traderelated measures the MEA authorizes will not impose burdens that developing countries cannot meet or that are disproportionate to the measure’s environmental benefits. For these reasons the trade community has become increasingly receptive to the notion that trade measures in MEAs, such as the POPs Convention, should be presumed consistent with Article XX. While this presumption is not reflected in any existing WTO cases, POPs negotiators should not let uncertainty deter them from adding trade measures to the mix of measures in the Convention. The decisions of GATT/WTO panels have indicated that while the WTO frowns upon unilateral measures, it might view multilateral measures, such as those authorized by a future POPs Convention, differently.3 Indeed, by including trade measures in the Convention and expressing the view that the WTO will defer to their decision to authorize the use of these measures, the negotiators will assist in 3 further cementing WTO acceptance of the MEA-deference interpretation of Article XX. Many of the countries negotiating the POPs Convention are also WTO Member States. Their expression through the Convention of an expectation of such deference will signal to the WTO strong Membership support for such an interpretation. Trade Measures in MEAs should automatically qualify for the WTO exception that measures that violate core obligations are WTO consistent if they are necessary to protect human animal or plant life or health The TBT and SPS Agreements promote harmonization of environmental measures by encouraging Members to base their measures on international standards. For measures that are governed by the TBT Agreement, those that are based on international standards are presumed not to create “unnecessary obstacles to trade” under the TBT Agreement.4 Conversely, laws that are not based on international standards do not qualify for this presumption. The SPS Agreement specifies that measures that conform to international standards are deemed necessary to protect human, animal or plant life or health and are presumed consistent with both the SPS Agreement and the GATT.5 For measures that are governed by the SPS Agreement, those not based on international standards must meet the risk assessment requirements imposed by the SPS Agreement. Like other international standards, MEAs encourage the harmonization of environmental measures, reducing trade tensions. MEAs should be considered “international standards” for the purposes of the SPS and TBT Agreements and measures taken pursuant to MEAs should be entitled to the presumption that they are consistent with those agreements. Such an understanding would also encourage States to become parties to MEAs. Measures required or authorized by an MEA, such as the POPs Convention, should be considered based on international standards, although it is not clear that they will be.6 Trade-related measures in MEAs should be considered “international standards” under the various WTO agreements and thus subject to deference from the WTO WTO AND ENVIRONMENTAL DISPUTES The WTO has a strong mechanism for challenging violations of the WTO rules No MEA has ever been challenged in the WTO When the WTO was created in 1995, the instrument that set the WTO apart from previous trade pacts was the increased power of the dispute settlement procedure. Member states can file complaints against trade practices of other Member states when it is felt that a Member is in breach of one of the numerous Agreements that make up the complicated trade rules of the WTO. The significant change from dispute settlement under previous trade agreements is that the new WTO dispute settlement system allows the WTO Dispute Settlement Body (DSB) to impose economic sanctions and penalties on Member states the DSB find to be in breach of any WTO Agreement. 4 Since the advent of the WTO the DSB has published the results of five environmental disputes. All of these challenges have resulted in a reversal of national environmental laws and policies in Member states that have been challenged. Despite the fact that several multilateral environmental agreements have directly banned or limited trade in hazardous substances, not one single challenge has ever been lodged with the DSB regarding these MEAs. Experts widely believe that this reflects a growing consensus among WTO Members that multilaterally negotiated and agreed upon measures to deal with environmental issues should never be challenged at the WTO. The DSB has been very clear about what it expects of WTO Members regarding multilateral environmental measures. In a dispute against the US in 1998 (Shrimp-Turtle), the Appellate Body first censured the US for its failure to engage in “serious across the board negotiations with the objective of concluding bilateral or multilateral agreements for the protection and conservation of sea turtles…7”. But the DSB urged Members to proceed with negotiations for multilateral environmental agreements “…we have not decided that sovereign states should not act together bilaterally, plurilaterally or multilaterally, either within the WTO or in other international fora, to protect… the environment. Clearly, they should and do.8” Nothing in the international trade rules or in the nature of the WTO prevents POPs negotiators from including trade-related measures in the POPs Convention, if negotiators believe that traderelated measures are needed to achieve the goals of the POPs Convention. To take trade measures off the table entirely is to allow the WTO rules – and the States that would use them to promote national economic interests over internationally agreed policy – to hinder the development of effective international policy to address POPs. ARTICLE D SHOULD INCLUDE TRADE-RELATED MEASURES WTO rules explicitly acknowledge that countries may take measures to protect human, animal and plant life and health and to conserve exhaustible natural resources, even when those measures might otherwise violate WTO rules, WTO rules acknowledge the importance of internationally arrived at environmental standards. POPs negotiators may wish to use trade-related measures as part of a mix of tools to achieve the goals of the POPs Convention. Trade-related measures can provide important strength to the POPs Convention when combined with incentives such as financial and technical assistance and may be necessary to promote the goals of the POPs Convention. The goal of POPs elimination, for example, will be undermined if export of POPs is permitted to countries not party to the POPs Convention, because the exported POPs will not be subject to the restrictions and phase-out obligations in the Convention. When trade-related measures are agreed to through a multilateral process, countries should not be allowed to turn to the WTO to undo the multilateral consensus. The WTO rules themselves explicitly acknowledge that countries may take measures to protect human, animal and plant life and health and to conserve exhaustible natural resources, even when those measures might otherwise violate WTO rules,9 and acknowledge the importance of internationally arrived at environmental standards.10 No multilateral environmental agreement (MEA) has ever been 5 directly challenged in the WTO, and experts widely believe that this is because any measure authorized under such an agreement would be presumed to be presumed WTO-consistent. POPs negotiators must be free to determine the best set of policy measures to achieve the goals of the POPs Convention – whether trade-related or not – unhindered by concerns that some states may use the WTO to second guess those measures. Article D.1: Prohibition of the Production and Use of certain POPs D. Measures to reduce or eliminate releases Prohibition of the production and use of certain persistent organic pollutants 1. [Subject to the accessibility of financial and technical assistance,] each Party shall [prohibit] [prohibit [and] [or] take [other] [the] legal measures necessary to eliminate] [take the legal measures necessary to eliminate], the production[, import, export] and use of the chemicals listed in Annex A (Elimination), in accordance with the provisions in that Annex. [1 bis. Each Party shall ensure that chemicals listed in Annex A, once their production and use have been banned, shall not be exported or imported except for the purpose of environmentally sound [destruction] [or] [disposal].] Prohibiting the import and export of POPs once their production and use is prohibited does not violate core GATT obligations and is crucial to achieving the goals of the POPs Convention Neither unbracketing the words “export, import” in D.1 nor the text in D.1 bis poses trade problems. Once domestic production and use of a substance are banned, no fatal issues of GATT inconsistency arise. An unqualified import and export ban of an illegal hazardous substances is protected by the environmental exception in GATT. Thus, once a country bans domestic production and use of a substance, it can ban imports and exports without violating the trade rules. The case of substances that are granted a limited exemption in Annex A is slightly more complicated, but still does not raise significant trade issues. The trade issues surrounding substances with a specific exemption in Annex A are the same as for those substances subject to the restricted use obligation in Article D.2 (listed in Annex B). Therefore, these issues are discussed together in the next section. Article D.2: Restrictions on the production and use of certain POPs D. Measures to reduce or eliminate releases Restrictions on the production and use of certain persistent organic pollutants 2. [Subject to the accessibility of financial and technical assistance,] each Party shall [prohibit] [prohibit [and] [or] take [other] [the] legal measures necessary to eliminate] [take the legal measures necessary to eliminate] the [production] [or] [and] use of the 6 chemicals listed in Annex B, (Restriction), except for the purposes specified therein, in accordance with the provisions in that Annex. Imports and exports of the chemicals listed in Annex B shall only be permitted between Parties and only for the purposes listed in Annex B or for their environmentally sound destruction. Restricting production and trade of restricted use chemicals under the POPs agreement is necessary to protect public health and the environment from the threat of POPs and is therefore justified under the environmental exceptions to the GATT In order to meet certain public health emergencies and other uses as provided for in Annex B, some countries have indicated that continued limited production of Annex B POPs may be required while alternatives are investigated. Not all of the countries that have in the past required access to Annex B POPs have either production capacity or stockpiles of the POP in question. Inevitably some limited trade in these substances will occur. The question is how far this trade can be limited to comply with the intent and the spirit of the POPs Convention without violating WTO/GATT provisions.11 Limiting trade in these substances only to parties to the POPs Convention violates the WTO Most Favored Nation (MFN) obligation. In the final analysis, however, such measures would likely be WTO consistent because they would qualify for protection under the GATT environmental exception for protection of life or health of humans, plants or animals (Article XX(b)). To qualify for this environmental exception, first the measure must be “necessary” to protect the life or health of humans, plants or animals. In the case of the POPs Convention, the international community has determined through a multi-year, multilateral process that an international solution to the problems posed by POPs is necessary. Countries are in the midst of negotiating rules for a multilateral Convention that may include trade-related measures. These trade measures will be an integral part of an overall design that the countries will have identified as necessary to protect human, animal and plant life and health and should easily pass WTO scrutiny. Consider, for example, the country using and producing an Annex B substance that bans imports of that substance from non-parties as provided in a future POPs Convention. Allowing trade in such substances only among parties will greatly enhance the parties’ ability to limit the use of these substances to those uses listed in Annex B. Because trade will only be permitted between parties, any substances that are produced or traded by the parties will be subject to the obligations in, and oversight mechanisms of, the POPs Convention. Such trade restrictions will better prevent the uncontrolled spread of POPs and enable more rapid and effective enforcement in cases of a breach of the obligations. Allowing trade only between parties will also create an incentive for some countries to join the Convention, particularly those that need assured access to Annex B chemicals for permitted uses. The more countries that join the Convention, the more these chemicals will be subject to the oversight of a multilateral system designed to minimize the dangers associated with their production and use, to provide assistance in obtaining less dangerous alternatives, and ultimately to eliminate these substances. If the POPs negotiators include such trade measures in the Convention, it will be for all these reasons, and probably more. Thus, the trade-related measures in the POPs Convention should be considered “necessary” within the meaning of the environmental exception. 7 The second step in qualifying for the environmental exceptions is that the measure must not be applied in a manner that constitutes either arbitrary or unjustifiable discrimination or a disguised restriction on international trade. As with the determination of “necessary,” the multilateral nature of the measure should lead to the presumption that the measure is neither arbitrarily nor unjustifiably discriminatory nor a disguised restriction on international trade. A multilaterally agreed-upon trade-related environmental measure, for the reasons discussed above, is not likely to be arbitrary or unjustifiable in its discrimination or to be designed to serve a hidden trade agenda. To the contrary, the measure will have been scrutinized by countries with varied interests and concerns. These countries will have designed the measure as necessary to achieve the goals of the agreement. Trade measures should be an integral part of an overall design participating countries have identified as necessary to protect human, animal and plant life and health and should pass WTO scrutiny. Article D.3: Measures dealing with POPs by-products Reduction in the release of persistent organic pollutants that are by-products [with the aim of their elimination] 3. Each Party shall [aim] [take all necessary measures] to reduce its [total] release [derived from anthropogenic sources] of each of the persistent organic pollutants that are by-products that are listed in Annex C [with the aim of their continuing minimisation and ultimate elimination] [consistent with its capacity and subject to the availability of technical and financial assistance]. To this end, each Party shall: (a) Promote the application of available measures that can expeditiously achieve a realistic and meaningful level of release reduction and/or source elimination by means that are feasible and practical. Such available measures may include, but are not limited to, incentive schemes such as: (i) labelling of products whose production created the by-products listed in Annex C , or whose production utilises clean production methods designed to reduce or eliminate POPs; or (ii) creation of public purchasing preferences for products whose production does not result in the formation of POPs, or which are not precursors to POPs Trade-related measures – such as labeling measures – authorized by an international agreement should be considered international standards within the meaning of the TBT and SPS Agreements The question of trade-related measures is most likely to arise in article D.3 in conjunction with national measures to implement the POPs Convention – for example, purchasing preferences or labeling schemes for products made in a way that does not produce dioxins, or products whose disposal will not lead to dioxin formation. These measures should be encouraged by the POPs negotiators by protecting them from attack at the WTO. The POPs negotiators can shield these 8 measures from the WTO by explicitly authorizing their use in the Convention so these measures will receive the same deference as other multilaterally agreed-upon trade-related environmental measures. Trade-related environmental measures authorized by MEAs should be presumed consistent with one or more of GATT’s environmental exceptions Such trade-related measures will receive the greatest deference in a dispute with the trade rules if they are explicitly required or authorized by the POPs Convention. These measures, arrived at through a multilateral process, are more likely to be equitably directed at the goal of POPs elimination than measures that a state unilaterally determines are necessary to achieve the goals of the POPs Convention. THE WTO SUPREMACY CLAUSE SHOULD BE REMOVED FROM THE POPS CONVENTION [N bis. Relationship with other agreements The provisions of this Convention shall not affect the rights and obligations of any Party deriving from any existing international agreements.] Supremacy clauses are not an appropriate tool to resolve the uncertainty regarding the relationship between trade measures in MEAs and the WTO rules To address the potential conflict with WTO rules – and resolve them in favor of trade concerns – some countries are supporting inclusion of a “WTO supremacy clause” (savings clause) in Article N bis of the POPs Agreement. The use of supremacy clauses in MEAs is a relatively recent development and is now regularly promoted by countries that wish to preserve their right to challenge trade measures taken to implement MEAs at the WTO. Supremacy clauses are not an appropriate tool to resolve the uncertainty regarding the relationship between trade measures in MEAs and the WTO rules. First, they fail to achieve the goal of reducing uncertainty. Simply affirming the integrity of existing international law does not address the numerous and complex questions about how MEAs and the WTO rules relate in specific instances. Such questions are better addressed by negotiators in the POPs negotiations process – where trade, environmental and public health expertise are all represented – than in a WTO dispute settlement proceeding. Second, supremacy clauses may deny MEAs equal status with WTO rules. The precise legal impact of the WTO supremacy clause will depend on future interpretations of MEAs and WTO rules. However, the aim of supremacy clause proponents is to place the rules of the multilateral trading system above those of the POPs Convention. Most dangerously, the inclusion of a supremacy clause in the POPs Convention might call into question the presumption that the WTO’s environmental exceptions apply to measures developed through MEAs, as discussed above. Simply by calling this presumption into question, supremacy clauses, and the countries that promote them, do great harm to the growing, yet still fragile, consensus at the WTO to ensure that trade rules are interpreted in a manner that accommodates environmental mandates developed through open, multilateral processes. Such clauses could persuade a WTO dispute 9 settlement panel to reject arguments to establish a presumption protecting trade-related measures in MEAs. A supremacy clause could also reverse the tacit position of many WTO Members that MEAs should never be challenged by the WTO. Some recently concluded MEAs12 have resolved the thorny political problem of inserting a WTO supremacy clause in the Articles of Agreement, by inserting language in the preamble that explicitly acknowledges a “non-hierarchy” in internationally agreed treaties. We would argue that enshrining this language in the preamble undermines the notion that MEAs are equal in status to the WTO rules and thus establish international standards within the meaning of the SPS and TBT Agreements and should automatically qualify for the exceptions in Article XX of the GATT. Such a compromise arguably still leaves MEAs open to challenge at the WTO – especially by WTO members who chose not to join the POPs Convention. Third, supremacy clauses may limit the effective implementation and enforcement of an MEA. The chilling effect of such a savings clause strenthens the hand of countries that prefer weak implementation of the POPs agreement. Finally, where conflicts arise between international trade agreements and MEAs, existing rules of treaty interpretation are available to resolve those conflicts. International law allows States to negotiate treaties that alter obligations under prior treaties or provide for more specific obligations. Under the rules of international law, where there is a conflict between two treaties, the later in time will prevail. Moreover, international law interprets conflict of law very narrowly. Where a subsequent treaty, such as the POPs Convention, addresses a specific problem that was not considered by the prior treaty (POPs for example were not considered in drafting the international trade agreements), the more specific agreement will apply. Thus POPs negotiators need not shy away from employing trade-related environmental measures where they deem such measures to be important to achieving the goals of the POPs Convention. CONCLUSION POPs negotiators and activists must defend the right to include trade measures in the POPs Convention. POPs negotiators and activists must ensure that these trade measures are not vulnerable to WTO attack after their adoption. Two important steps can be taken to protect the POPs Convention from challenge in the WTO. First, POPs negotiators should ensure that the POPs Convention does not contain a WTO supremacy clause, as is currently proposed in article N bis of the draft POPs Convention. Second, negotiators should explicitly and carefully review all trade measures suggested for inclusion in the POPs Convention. At a minimum the review process should consider less trade-restrictive alternatives and demonstrate their flaws in attaining the goals of the POPs Convention. 1 See UNEP, Trade related environmental measures in the field of safety in biotechnology, Environment and Trade Monograph No. 14 (1997); for a more in depth discussion of the relationship between trade measures in MEAs and the trade rules, see CIEL, Trade Measures and Multilateral Environmental Agreement: Resolving Uncertainty and Removing the WTO Chill Factor (WWF International Discussion Paper, November 1999); for a more in depth discusion of this argument see Saladin & Van Dyke, International Trading Rules and the POPs Convention (CIEL Issue Brief, November 1999) 2 See, e.g., Robert Housman & Donald M. Goldberg, Legal Principles in Resolving Conflicts Between Multilateral Environmental Agreements and the GATT/WTO, in ENVIRONMENT AND TRADE 10: THE USE OF TRADE MEASURES IN SELECTED MULTILATERAL ENVIRONMENTAL AGREEMENTS 297 (CIEL & UNEP: Washington, D.C. 1995). 10 3 A challenge to a US sea turtle protection law prevailed in a dispute before the WTO, in part because the United States had failed to exhaust multilateral options in its efforts to protect sea turtles, before imposing a unilateral protection strategy. United States – Import Prohibition of Certain Shrimp and Shrimp Products, WT/DS58/AB/R [hereinafter Shrimp-Turtle]. 4 Agreement on Technical Barriers to Trade, art. 2.5, April 15, 1994 [hereinafter TBT Agreement], available at URL: <http://www.wto.org/wto/legal/finalact.htm>. 5 See Agreement on the Application of Sanitary and Phytosanitary Measures, art. 3.3, April 15, 1994 [hereinafter SPS Agreement], available at URL: <http://sss.wto.org/goods/spsagr.htm>. 6 For a more detailed discussion of this argument see Saladin & Van Dyke, supra note 1. 7 Shrimp-Turtle supra note 3, at 166. 8 See Shrimp-Turtle supra note 3, at 185. 9 See General Agreement on Tariffs and Trade (GATT), art. XX(b) & (g), Oct. 30, 1947, available at URL: <http://www.wto.org/wto/legal/finalact.htm>. 10 See, e.g., SPS Agreement art. 3.3, TBT Agreement art. 2.2. 11 Other MEAs that include trade prohibitions and restrictions include, for example, the Montreal Protocol, The Bamako Convention and the Basle Convention. 12 See Convention On The Prior Informed Consent Procedure for Certain Hazardous Chemicals and Pesticides In International Trade (1998), and Cartagena Protocol On Biosafety (2000). 11