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婵犵數鍋涢ˇ鏉棵洪弽顐n偨闁靛濡囬埞宥夋煃閳轰礁鏆曠紒鎲嬫嫹 | 婵犵數鍋涢ˇ鏉棵洪弽顐n偨闁靛鏅涘Λ妯好归悡搴f憼妞わ讣鎷� | 婵犵鍓濋〃鍛存偋閸涱垱顐介柨鐕傛嫹 | 缂傚倷绶¢崰妤呭磿閹惰棄绠圭憸鏂款嚕椤掑嫬鐐婇柍鍝勫暙婵烇拷 | 闂備礁鎲$敮妤呭垂瀹曞洩濮抽柕濞垮劗閺嬫牠鏌¢崶鈺佷户濞寸》鎷� | 婵犳鍠楄摫闁搞劌纾懞閬嶅Ω閵夈垺鐏冮梺鍝勬川閸嬬喐瀵奸敓锟� | 缂傚倸鍊风粈浣烘崲閹寸姷鐭堥柣鐔稿閺嬫牠鏌¢崶鈺佷户濞寸》鎷� | 闂佽崵鍋炵粙鎴﹀嫉椤掑嫬妫橀柛灞惧焹閺嬫牠鏌¢崶鈺佷户濞寸》鎷� | 闂佽崵濮村ú銈壦囬幎绛嬫晩闁圭偓鏋奸弸鏍煛閸モ晛浠уù纭锋嫹 | 闂備礁鎲¢懝楣冩偋閸曨垰鐒垫い鎴f娴滈箖姊洪棃娑欘棏闁稿鎹囬弻娑橆潩閻愵剙顏� | 婵犵鍓濋〃鍛存偋閸涱垱顐介柕澹啫鐏婃俊銈忕到閸熺娀宕戦幘缁樻櫢闁跨噦鎷� | 婵犵數鍋涢ˇ鏉棵洪弽顐n偨闁靛鏅涘Λ姗€鏌涢妷顖滅暠濠殿噯鎷� | 闂備礁鎲¢懝楣冩偋閸℃稑绠栭柟鍓х帛閸ゆ垿鏌涢幇銊︽珕闁瑰嚖鎷� | 婵犵數鍋涢ˇ鏉棵洪弽顐n偨闁靛/鍕濠殿喗绻傞惉鐓幬i敓锟� | 闂備礁鎲¢悷锕傛偤閺囥垹鐒垫い鎺嗗亾闁哥喐鎸抽妴鍌炴嚍閵夛箑鍔呴梺璺ㄥ櫐閹凤拷 | 
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环境与贸易

  There two issues is noteworthy, first one is what can influence an MEA.
  “One is the need for a clear understanding of the meaning and coverage of the term ‘environment’ in this context. The other is what constitutes a genuine ‘multilateral’ consensus in an MEA.” This is important since a broad enough consensus is likely to produce a well-balanced multilateral agreement and a robust outcome. Although there may be no simple formula that can be applied to every case, preliminary discussions on this point have indicated that negotiation of and participation in an MEA should be open on equitable terms to all countries, and that the participation of interested countries should be numerous and broad in geographical terms and in terms of countries at varying levels of development. It has been suggested that consideration might also be given to adequate representation of consumer and producer nations of the products covered by an MEA among an MEA’s signatories, or ensuring, as in commodity arrangements, that the bulk of international trade was represented by signatories.
  Another one is what extent a trade measure should be specified in an MEA whether it is to be cleared under this approach. It has been pointed out that few MEAs to date include mandatory obligations for the use of specific trade measures. Even those that do, for example by directing signatories to use quantitative restrictions or import or export licensing schemes, still permit a wide range of individual discretion.
  C. Tuna-Dolphin Case
  In eastern tropical areas of the Pacific Ocean, schools of yellow fin tuna often swim beneath schools of dolphins. When tuna is harvested with purse seine nets, dolphins are trapped in the nets. They often die unless they are released.
  The US Marine Mammal Protection Act sets dolphin protection standards for the domestic American fishing fleet and for countries whose fishing boats catch yellow fin tuna in that part of the Pacific Ocean. If a country exporting tuna to the United States cannot prove to US authorities that it meets the dolphin protection standards set out in US law, the US government must embargo all imports of the fish from that country. In this dispute, Mexico was the exporting country concerned. Its exports of tuna to the US were banned. Mexico complained in 1991 under the GATT dispute settlement procedure.
  The embargo also applies to “intermediary” countries handling the tuna en route from Mexico to the United States. Often the tuna is processed and canned in a one of these countries. In this dispute, the “intermediary” countries facing the embargo were Costa Rica, Italy, Japan and Spain, and earlier France, the Netherlands Antilles, and the United Kingdom. Others, including Canada, Colombia, the Republic of Korea, and members of the Association of Southeast Asian Nations, were also named as “intermediaries”.


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