European Union's Emission Trading System Term Paper

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European Union's Emission Trading System

What is the stated purpose behind the EU ETS?

The EU ETS has been a cap and trade method made to incentivise economical cutbacks in greenhouse gas emissions (GHG) coming from carbon-intensive industrial sectors as well as electrical power generators. Proof shows that the executive load (the expense of checking, confirming and validation of emissions and costs to government bodies) involving the EU ETS upon smaller sized emitters has been disproportionately big. Article 27 involving the EU ETS Directive offers a great opt out via the EU ETS in Phase III (2013-2020) to lessen the executive burdens upon small-scale emitters as well as hospitals. It entails that opted out setups deal with procedures which attain a similar share to emissions cutbacks as though the setup had been still within the EU ETS. The aim in providing an opt-out has been to incentivise GHG pollutants cutbacks while reducing the regulating price burdens towards UK small-scale emitters as well as hospitals. The goal has been to do this while achieving EU legal specifications, not considerably influencing the emissions cutbacks accomplished by providers within the EU ETS as well as making certain UK business has been not positioned in a competitive downside when compared with companies within the EU. Within the restrictions related to the EU ETS Directive, these 243 qualified operators who've selected to opt-out related to the ETS in Phase III will probably be recommended to decrease emissions with a substitute measure (EU ETS, 2008).

Why do you agree or disagree with the concept of the EU ETS?

Those activities that are protected have been electrical power pursuits (which includes combustion setups, coke stoves as well as mineral oil refineries); generation as well as refinement of ferrous alloys; mineral industrial sectors (which includes concrete, lime, glass, as well as ceramics); and manufacturing of pulp as well as paper (EU ETS, 2007).

The overall principle has been that the activity is going to be regarded as a part of an agenda 1 activity whether it has been a built-in element of that Schedule 1 process. In thinking about whether or not a task has been a built-in element of an agenda 1 activity the subsequent elements will probably be pertinent (EU ETS, 2007):

• whether or not the Schedule 1 process could be practically feasible devoid of that process e.g. In which the manufacturing of paper (process 4.2 within Schedule 1 towards the ETS Polices) wouldn't be feasible devoid of an on-site CHP plant supplying heavy steam; as well as

• whether or not the activity's main objective has been the Schedule 1 process e.g. The main objective related to the CHP plant has been to create heavy steam to be used within the manufacturing of paper. The government bodies will need to pass a practical method of defining "main objective," even though generally it will likely be understood to be the highest percentage of their results (EU ETS, 2007).

Nevertheless, this method has resulted in disparities in scope throughout the EU and elevated expenses in certain areas. There has been broad consensus throughout The European Union that the easiest method to solve the two problems has been to incorporate each and every emission resource on-site. This eliminates the possibility of setups within as well as amid Member States to generally be handled in a different way and records extra co2 emissions, frequently lowering the expenses of monitoring as well as reporting within the procedure. Because of the short time offered, the method laid out above will continue to be for almost all setups within the UK for Phase II. Nevertheless, growth provides a chance to improve harmonisation in certain market sectors (EU ETS, 2007).

What are the current and potential environmental results of the EU ETS?

The EU ETS has been made to assist installations throughout the EU to provide emissions cutbacks at the very least price. Besides the expenses of conformity, operators taking part within the ETS have been susceptible to the expense associated with monitoring, reporting as well as validation (MRV) and also the charges caused by competent government bodies in Member States' recuperating the expense of managing the program. The job of operators and also the competent regulators to provide suitable MRV has been necessary to making certain the credibility of emissions cutbacks and guarding the economical as well as environmental stability involving the program (Impact Assessment, 2012).

Nevertheless it continues to be accepted in Europe that the management expenses challenged by small-scale emitters underneath the EU ETS have been disproportionately higher per tonne of CO2, when compared to expenses for setups with bigger pollutants. It has been shown within the UK, immediately after an evaluation involving the management expenses to UK operators throughout Phases I (2005-2007), as well as II (2008-2012) related to the ETS. Within the UK, this evaluation discovered that small-scale emitters comprising two percent of pollutants sustained roughly twenty percent of the overall management load (over the sixty percent of all setups protected by the evaluation). The biggest eight percent of emitters had been accountable for sixty percent of emissions as well as sustained forty five percent of the management load Per tonne of CO2 released, the approximated management expenses for UK small-scale emitters surpassed £1, whilst expenses for UK big emitters had been estimated to generally be £0.04. Just about all UK hospital setups have been additionally small-scale emitters and for that reason confront exactly the same excessive management price load per tonne of CO2 (Impact Assessment, 2012).

What other effects have occurred because of the EU ETS?

The food as well as drink market has not been explicitly placed in Schedule 1. Nevertheless, a food producer has 2 boilers of four mega watts and five mega watts and 2 generators of five mega watts as well as eight mega watts on-site. (Observe that all mega watts (MW) statistics refer to ranked thermal input). Since the boilers as well as generators have all been the exact same Schedule 1 process (combustion) and have all been managed from the exact same operator as well as have been on the very same site; their volumes have been aggregated jointly (despite the fact that there might be no technical link amid those activities). The boilers as well as generators will successfully be handled as one individual fixed technical system and because the overall volume has been more than twenty mega watts (22MW), the installation is going to be integrated within the EU ETS (as being a combustion setup) (EU ETS, 2007).

University grounds - The volumes of combustion units throughout University grounds have been aggregated in which the university under consideration has been viewed as one common location. This is applicable even where buildings have been divided by roads and also the units have not been technically linked however the area under consideration has been section of the university's common location (EU ETS, 2007).

Why or why not should the U.S. participate in the EU ETS?

Responding to the witnessed drop in costs, numerous marketplace experts as well as stakeholders started publicly pondering if the carbon cost has not been "too low," has been adequate to incentivise low carbon funding for future years, and perhaps must be backed by way of some type of direct involvement within the marketplace. Subsequently, on December 20th, the EU Parliament's ENVI Panel officially suggested that changes be made in the Electrical power Effectiveness Directive to pull away a substantial volume of wages via the marketplace throughout Phase 3. The suggested validation had been "to make amends for the enactment of [the Electrical power Efficiency] Directive" as well as "to recover the cost mechanism to amounts imagined within the influence evaluation." In reaction, the marketplace at first surged - with EUA costs increasing thirty percent the…

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"European Union's Emission Trading System" (2012, December 16) Retrieved January 18, 2017, from

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"European Union's Emission Trading System", 16 December 2012, Accessed.18 January. 2017,