17 resultados para International Tax Regime

em Archive of European Integration


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Questions regarding oil spills remain high on the political agenda. Legal scholars, legislators as well as the international, European and national Courts struggle to determine key issues, such as who is to be held liable for oil spills, under which conditions and for which damage. The international regime on oil spills was meant to establish an “equilibrium” between the needs of the victims (being compensated for their harm) and the needs of the economic actors (being able to continue their activities). There is, however, a constantly increasing array of legal scholars’ work that criticizes the regime. Indeed, the victims of a recent oil spill, the Erika, have tried to escape the international regime on oil spills and to rely instead on the provisions of national criminal law or EC waste legislation. In parallel, the EC legislator has questioned the sufficiency of the international regime, as it has started preparing legislative acts of its own. One can in fact wonder whether challenging the international liability regime with the European Convention on Human Rights could prove to be a way forward, both for the EC regulators as well as the victims of oil spills. This paper claims that the right to property, as enshrined in Article P1-1 of the Human Rights Convention, could be used to challenge the limited environmental liability provisions of the international frameworks.

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Like other regions of the world, the EU is developing biofuels in the transport sector to reduce oil consumption and mitigate climate change. To promote them, it has adopted favourable legislation since the 2000s. In 2009 it even decided to oblige each Member State to ensure that by 2020 the share of energy coming from renewable sources reached at least 10% of their final consumption of energy in the transport sector. Biofuels are considered the main instrument to reach that percentage since the development of other alternatives (such as hydrogen and electricity) will take much longer than expected. Meanwhile, these various legislative initiatives have driven the production and consumption of biofuels in the EU. Biofuels accounted for 4.7% of EU transport fuel consumption in 2011. They have also led to trade and investment in biofuels on a global scale. This large-scale expansion of biofuels has, however, revealed numerous negative impacts. These stem from the fact that first-generation biofuels (i.e., those produced from food crops), of which the most important types are biodiesel and bioethanol, are used almost exclusively to meet the EU’s renewable 10% target in transport. Their negative impacts are: socioeconomic (food price rises), legal (land-grabbing), environmental (for instance, water stress and water pollution; soil erosion; reduction of biodiversity), climatic (direct and indirect land-use effects resulting in more greenhouse gas emissions) and public finance issues (subsidies and tax relief). The extent of such negative impacts depends on how biofuel feedstocks are produced and processed, the scale of production, and in particular, how they influence direct land use change (DLUC) and indirect land use change (ILUC) and the international trade. These negative impacts have thus provoked mounting debates in recent years, with a particular focus on ILUC. They have forced the EU to re-examine how it deals with biofuels and submit amendments to update its legislation. So far, the EU legislation foresees that only sustainable biofuels (produced in the EU or imported) can be used to meet the 10% target and receive public support; and to that end, mandatory sustainability criteria have been defined. Yet they have a huge flaw. Their measurement of greenhouse gas savings from biofuels does not take into account greenhouse gas emissions resulting from ILUC, which represent a major problem. The Energy Council of June 2014 agreed to set a limit on the extent to which firstgeneration biofuels can count towards the 10% target. But this limit appears to be less stringent than the ones made previously by the European Commission and the European Parliament. It also agreed to introduce incentives for the use of advanced (second- and third-generation) biofuels which would be allowed to count double towards the 10% target. But this again appears extremely modest by comparison with what was previously proposed. Finally, the approach chosen to take into account the greenhouse gas emissions due to ILUC appears more than cautious. The Energy Council agreed that the European Commission will carry out a reporting of ILUC emissions by using provisional estimated factors. A review clause will permit the later adjustment of these ILUC factors. With such legislative orientations made by the Energy Council, one cannot consider yet that there is a major shift in the EU biofuels policy. Bolder changes would have probably meant risking the collapse of the high-emission conventional biodiesel industry which currently makes up the majority of Europe’s biofuel production. The interests of EU farmers would have also been affected. There is nevertheless a tension between these legislative orientations and the new Commission’s proposals beyond 2020. In any case, many uncertainties remain on this issue. As long as solutions have not been found to minimize the important collateral damages provoked by the first generation biofuels, more scientific studies and caution are needed. Meanwhile, it would be wise to improve alternative paths towards a sustainable transport sector, i.e., stringent emission and energy standards for all vehicles, better public transport systems, automobiles that run on renewable energy other than biofuels, or other alternatives beyond the present imagination.

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Trade is a key element of the development policy of the European Union (EU). As the most important trading partner of developing countries, the EU attempts to facilitate the participation of developing countries in global trade and contribute to economic growth through providing market access and financial assistance. For twenty-five years, the commitment of the EU was largely focused on its former colonies, more specifically in Africa, the Caribbean and the Pacific (ACP). The developing world, in terms of the EU’s trade policy, was therefore divided between ACP states with special provisions under the Lomé Conventions and all other developing countries. With the new millennium, this special relationship came to an end. Pressure from several member states1 and the World Trade Organization (WTO) led to an overhaul of the EU’s trade regime vis-à-vis developing countries and to the loss of the privileged position of ACP countries. The result of this overhaul is still pending. Economic Partnership Agreements (EPAs) – to be negotiated between the EU and several ACP regions – have only been realized in the Caribbean. This article will to examine the negotiations between the EU and West Africa and discuss the interests involved on the African side. Following the introduction, the second part of this article is dedicated to the Lomé Conventions with a focus on the change occurring from the third to the fourth revision in order to understand the current situation. The third part is going to take a look at the Cotonou agreement and the trade regime of the EU in general before turning to the negotiations for an Economic Partnership Agreement between the EU and West Africa. The conclusion summarizes the main findings.

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As the US and its allies France and Turkey dither over whether or not to punish Assad for having used sarin gas to kill his own people, the crucial question is: What response might the outside world legally take without the authority of the UN Security Council, which remains blocked by two veto-wielding members, Russia and China? Sadly, international law provides no clear-cut answers to this dilemma. To respond to what US Secretary of State John Kerry has rightly called a “moral obscenity”, this commentary explores ways in which formal interpretations of international law might give way to a more pragmatic approach to punish the Assad regime for its use of chemical weapons.

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One complement to domestic climate policies could be the regulation of carbon dioxide emissions arising during the production of imported products. Such ‘border carbon adjustments’ (BCAs) are said to have several benefits, but are also severely criticised. This Policy Brief highlights some weaknesses in the standard argumentation for BCAs. But there is an alternative argument for border carbon measures, based on the fact that countries expose each other to climate externalities. The reformulated argument is economically more convincing, and provides a more convincing justification for the extraterritorial feature of border carbon measures. However, there are also several important factors mitigating against the implementation of such measures, including the risk that these measures will be used for protectionism. One complement to domestic climate policies could be the regulation of carbon dioxide emissions arising during the production of imported products. Such ‘border carbon adjustments’ (BCAs) are said to have several benefits, but are also severely criticised. This Policy Brief highlights some weaknesses in the standard argumentation for BCAs. But there is an alternative argument for border carbon measures, based on the fact that countries expose each other to climate externalities. The reformulated argument is economically more convincing, and provides a more convincing justification for the extraterritorial feature of border carbon measures. However, there are also several important factors mitigating against the implementation of such measures, including the risk that these measures will be used for protectionism.

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Measures undertaken by the Belarusian government in the areas of the economy, internal affairs and foreign policy in recent months have proven increasingly ineffective. Despite the deteriorating macroeconomic situation, Minsk is not implementing the reforms necessary to combat the crisis and its activity is limited only to feigned actions and administrative regulations. As a result, the economic situation is worsening but the chances of obtaining external loans as support, for example from the International Monetary Fund (IMF), are decreasing. At the same time there is mounting fear among the regime of social unrest, therefore by raising salaries of the least well-off groups of citizens it is trying to compensate for the increased costs of living. On the other hand, the government is extending the scope of control over society and competences of enforcement bodies. Belarus’s room for manoeuvre in foreign policy has also been diminishing substantially. Despite the EU’s declared willingness to reach an agreement and its encouragement, Lukashenko is not ready to make concessions in the political sphere (e.g. to rehabilitate political prisoners), and this is hindering the normalisation of relations with the West. Minsk furthermore feels a mounting pressure from Moscow, making the Belarusian negotiating position ever weaker. The lack of freedom of manoeuvre in foreign policy, no possibility to maintain a costly economic model and the lack of support from the majority of society all prove that Alexander Lukashenko’s regime is in severe crisis. The system he established is no longer able to respond to current threats with adequate and effective strategies. This situation is challenging the regime’s stability and calls into question its viability in the longer term.

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Sufficient cross‐border electricity transmission infrastructure is a pre‐requisite for a functioning European internal market for electricity. Also, the achievement of the EU’s energy policy objectives – sustainability, competitiveness and security of supply – critically depends on adequate investment in physical interconnections between the member states. Mainly focusing on the “regulatory path”, this paper assesses different ways to achieve a sufficient level of interconnector investment. In a first step, economic analysis identifies numerous impediments to interconnector investment adding up to an “interconnector investment failure”. Reflecting on the proper regulatory design of an EU framework able to overcome the interconnector investment failure, a number of recommendations are put forward:  All congestion rents should be channeled into interconnector building. Unused rents should be transferred to a European interconnector fund supervised by an EU agency.  Even though inherently sub‐optimal, merchant transmission investment can be used as a means to put pressure on regulated transmission system operators (TSO) that do not deliver. An EU agency should have exclusive competence on merchant interconnector exemptions.  A European TSO organization should be entrusted with supra‐national network planning, supervised by an EU agency.  The agency should decide on investment cost reallocation for interconnector projects that yield strong externalities. Payments could be settled via a European interconnector fund.  In case of non‐compliance with the supra‐national network plan, the EU agency should have the right to organize a tender – financed by the European interconnector fund – in order to get the “missing link” built. Assessing the existing EU regulatory framework, the efforts of the 2009 “third energy package” to fill the “regulatory gap” with new EU bodies – ACER and ENTSO‐E – are acknowledged. However, striking holes in regulatory framework are spotted, notably with regard to the use of congestion rents, interconnector cost allocation, and the distribution of decision making powers on new infrastructure exemptions A discussion of the TEN‐E interconnector funding scheme shows that massive funding can be an interim solution to the problem of insufficient interconnection capacities while overcoming the political deadlock on sensible regulatory topics such as interconnector cost allocation. The paper ends with policy recommendations.