چگونگی یک تنظیم مرزی سیستم انتشار تجاری برای اتحادیه اروپا طراحی کنیم ؟
|کد مقاله||سال انتشار||تعداد صفحات مقاله انگلیسی||ترجمه فارسی|
|19723||2010||9 صفحه PDF||سفارش دهید|
نسخه انگلیسی مقاله همین الان قابل دانلود است.
هزینه ترجمه مقاله بر اساس تعداد کلمات مقاله انگلیسی محاسبه می شود.
این مقاله تقریباً شامل 8488 کلمه می باشد.
هزینه ترجمه مقاله توسط مترجمان با تجربه، طبق جدول زیر محاسبه می شود:
Publisher : Elsevier - Science Direct (الزویر - ساینس دایرکت)
Journal : Energy Policy, Volume 38, Issue 9, September 2010, Pages 5199–5207
Border adjustments are currently discussed to limit the possible adverse impact of climate policies on competitiveness and carbon leakage. We discuss the main choices that will have to be made if the European Union implements such a system alongside the EU ETS. Although more analysis is required on some issues, on others some design options seem clearly preferable to others. First, the import adjustment should be a requirement to surrender allowances rather than a tax. Second, the general rule to determine the amount of allowances per ton imported should be the product-specific benchmarks that the European Commission is currently elaborating for a different purpose (i.e. to determine the amount of free allowances). Third, this obligation should apply when the imported product is registered at the EU border, and not after the end of the year as is the case for domestic emitters. Fourth, the export adjustment should take the form of a rebate on the amount of allowances a domestic emitter has to surrender. Five, this rebate should equal the above-mentioned product-specific benchmarks, not the emissions of the particular exporting plant or firm. Finally, the adjustment does not have to apply to consumer products but mostly to basic products.
Whether or not an agreement is reached at the ongoing UNFCCC climate negotiations, it is very unlikely that a single global price for greenhouse-gas emissions will prevail. First, some countries may refuse to ratify a future treaty. Second, a treaty will certainly put different types of targets on countries with different development levels, following the principle of common but differentiated responsibilities. Third, parties to a treaty will most likely remain free to choose whether or not emissions from greenhouse-gas (GHG) intensive industries are regulated under an emission trading scheme or under other policy measures. At least in theory, a persistent CO2 price differential may change trade patterns, i.e. reduce sales of firms subjected to the highest CO2 price in favour of those exposed to a smaller (or nil) CO2 price, and induce what is called carbon leakage. Whilst evidence of such leakage is presently limited (Ellerman et al., 2009, Hourcade et al., 2008 and Reinaud, 2008), industry groups and policy makers are concerned with the perceived adverse competitiveness implications of the European Union Emissions Trading Scheme (EU ETS). For this reason, Directive 2009/29/EC, which revises the EU ETS, includes some provisions to limit carbon leakage. The main one is the continued free allowance allocation to the “sectors or subsectors which are exposed to a significant risk of carbon leakage” (Article 10a–12). However, the Directive also states that “By 30 June 2010, the Commission shall […] submit to the European Parliament and to the Council […] any appropriate proposals, which may include […] inclusion in the Community scheme of importers of products which are produced by the sectors or subsectors [exposed to a significant risk of carbon leakage]”. In other words, the Directive mentions, although cautiously, a border adjustment (BA) for GHG-intensive imports.2 In the USA, the Waxman–Markey bill adopted by the House of Representatives includes more concrete provisions. If no international agreement on climate change has been reached by January 1, 2018, the president of the United States is required to set up an “international reserve allowance program.” From 2020 on, imports in a covered sector would be prohibited unless the importer has obtained an “appropriate” amount of emission allowances from the international reserve allowance program. This requirement can be defined as BA. It would not apply, however, to imports from countries that (1) have signed an international agreement with the United States that imposes economy-wide restrictions on greenhouse-gas emissions that are at least as stringent as those in the United States; (2) have signed a multilateral or bilateral emission-reduction agreement with the United States for the sector in question; (3) have an annual energy or greenhouse-gas intensity in that sector that is less than or equal to that of the equivalent US sector; (4) are classified as the least-developed of developing countries; (5) are responsible for less than 0.5% of total global greenhouse-gas emissions and less than 5% of US imports of covered goods in the sector (James, 2009 and van Asselt and Brewer, 2010). Similarly, the cap-and-trade bills introduced in the US Senate also include provisions for border adjustments, although with less details. This is the case of S. 1733, the Clean Energy Jobs and American Power Act introduced by Senators Kerry and Boxer on October 23, 2009 (Larsen et al., 2009) and of S. 2877, the Carbon Limits and Energy for America’s Renewal Act introduced by Senators Cantwell and Collins on December 11, 2009. For instance, the latter proposes an adjustment for both imports, through a “border carbon adjustment”, and exports, through a “targeted relief fund for exporters” (Larsen and Bradbury, 2010). More generally, a BA is a trade measure designed to level the playing field between domestic producers facing costly climate policy and foreign producers with no or little constraint on their GHG emissions. A growing body of literature (e.g. Ismer and Neuhoff (2007), Godard (2007), Demailly and Quirion, 2007 and Demailly and Quirion, 2008, Mattoo et al. (2009)) as well as some stakeholders (ETUC, 2008) have come to the conclusion that a BA may effectively prevent climate policies from negatively impacting European industry competitiveness, although some analyses come to the opposite conclusion (Weber and Peters, 2009, and references therein). BAs are also sometimes presented as a way for the EU to induce other countries to participate in an international climate protection agreement (Stiglitz, 2006). However, some experts come to an opposite conclusion since a BA may be seen as a trade sanction by developing countries and may thus threaten the goodwill in international climate negotiations (Droege et al., 2009). As a trade measure, a BA may be contested by a member of the World Trade Organization (WTO) before the WTO dispute settlement mechanism. The basis or cause of action for a WTO dispute must be found in the “covered agreements”, including the General Agreement on Tariffs and Trade (GATT). The WTO Dispute Settlement Process is too complex to be detailed here but is described in WTO (2010). The priority is to settle disputes preferably through a mutually agreed solution, but if no such solution is found and if the losing party fails to comply with the WTO ruling, the prevailing member may receive the right to impose trade sanctions. Here again, recent analyses conclude that the design details of a BA will be key in determining whether it would be accepted by a WTO dispute panel (De Cendra De Larragán, 2006, Pauwelyn, 2007, et al., 2008 and UNEP and WTO, 2009). The aim of the present paper is not to conclude on the opportunity for the EU to implement a border adjustment. Rather, its aim is to discuss the main design options of a BA in complement to the EU ETS, if the EU decides to implement one. The criteria to discuss these options are their capacity to limit carbon leakage and their likelihood to be accepted by a WTO dispute panel. When relevant, we also discuss whether these design options are more likely to inhibit or to favour the international climate negotiation, and their administrative cost. Throughout this paper, we assume that allowances are fully auctioned. Firstly, a BA is much more difficult to justify under free allocation than under auctioning. Indeed, combining a BA with free allocation would mean either that foreign producers would receive no free allowances, hence that EU producers would be unduly advantaged, which the WTO would probably reject, or that the EU would allocate free allowances to foreign producers, which seems politically highly unlikely. Secondly, with a BA the European industry does not suffer from a competitive disadvantage (or much less so), there is thus little rationale for free allocation, which creates economic distortions (Matthes and Neuhoff, 2008). Godard (2007) and Genasci (2008) make proposals for a BA in case of a hybrid allocation with both freely allocated and auctioned allowances.3 The rest of the paper is structured as follows. The first part aims at clarifying the notions of competitiveness and carbon leakage used throughout the paper. In the second part, we list and discuss the different elements that require being defined, in order to implement a BA in complement to the EU ETS. More precisely we discuss: whether it should be based on taxes or allowances (Section 2.1) whether it should cover only imports or also exports (Section 2.2); the targeted products (Section 2.3); the adjustment base (Section 2.4); the countries covered (Section 2.5); the enforcement issues specific to the border adjustment (Section 3.1) and finally the administration cost (Section 3.2). The last part concludes and offers further research questions.
نتیجه گیری انگلیسی
Whereas several papers recently addressed the pros and cons of border adjustments, few elaborate on the design of such systems. From this survey on the design issues of a border adjustment, we find no reason to conclude that they would be unmanageable. Moreover, we conclude that some design options seem clearly preferable. In particular, (i) the import adjustment should take the form of a requirement to surrender allowancesrather than of a tax; (ii) this obligation should apply when the imported product is registered at the EU border, not four months after the end of the year as for domestic emitters; (iii) the general rule to determine the amount of allowances per ton imported should be the product-specific benchmarks that the European Commission is currently elaborating for a different purpose (i.e. to determine the amount of free allowances in the EU ETS); (iv) the export adjustment should take the form of a rebate on the amount of allowances a domestic emitter has to surrender or a refund of allowances to the exporter when different from the emitter; (v) the adjustment does not have to apply to consumer products such as cars or appliances, but mostly to basic materials. However, more analysis is clearly required on some issues, mainly (i) the precise products coverage, especially for chemical products and for downstream steel and aluminium products; (ii) whether steel and aluminium scrap should be included; (iii) whether foreign firms, which can prove that they have lower unitary emissions than the EU average, should have a lower adjustment; (iv) how to quantify indirect emissions from electricity; (v) how to make the border adjustment multilateral, i.e., to have it cover all countries participating in the climate agreement or, in the absence of a comprehensive agreement, to have it cover all major emitting countries; (vi) whether or not the receipts from the import adjustment be earmarked for exporting countries, and whether or not an exemption should be made for products covered by a similar export tax in their country of origin.