The EU emissions trading system (EU ETS) is a cornerstone of the EU's policy to combat climate change and its key tool for reducing greenhouse gas emissions cost-effectively. It is the world's first major carbon market and remains the biggest one.
The EU ETS:
The EU ETS works on the 'cap and trade' principle.
A cap is set on the total amount of certain greenhouse gases that can be emitted by installations covered by the system. The cap is reduced over time so that total emissions fall.
Within the cap, companies receive or buy emission allowances which they can trade with one another as needed. They can also buy limited amounts of international credits from emission-saving projects around the world. The limit on the total number of allowances available ensures that they have a value.
After each year a company must surrender enough allowances to cover all its emissions, otherwise heavy fines are imposed. If a company reduces its emissions, it can keep the spare allowances to cover its future needs or else sell them to another company that is short of allowances.
Trading brings flexibility that ensures emissions are cut where it costs least to do so. A robust carbon price also promotes investment in clean, low-carbon technologies.
Set up in 2005, the EU ETS is the world's first international emissions trading system. It remains the biggest one, accounting for over three-quarters of international carbon trading.
The EU ETS is also inspiring the development of emissions trading in other countries and regions. The EU aims to link the EU ETS with other compatible systems.
The EU ETS has proved that putting a price on carbon and trading in it can work. Emissions from installations in the system are falling as intended – by slightly over 8% compared to the beginning of phase 3 (see 2016 figures).
In 2020, emissions from sectors covered by the system will be 21% lower than in 2005.
In 2030, under the revised system they will be 43% lower.
The system covers the following sectors and gases with the focus on emissions that can be measured, reported and verified with a high level of accuracy:
Participation in the EU ETS is mandatory for companies in these sectors, but
The EU ETS is now in its third phase, which is significantly different from phases 1 and 2.
The main changes from the previous two phases are:
The legislative framework of the EU ETS for its next trading period (phase 4) was revised in early 2018 to enable it to achieve the EU's 2030 emission reduction targets in line with the 2030 climate and energy policy framework and as part of the EU's contribution to the 2015 Paris Agreement.
The revision focuses on:
The aim of the EU Emissions Trading System (EU ETS) is to help EU Member States achieve their commitments to limit or reduce greenhouse gas emissions in a cost-effective way. Allowing participating companies to buy or sell emission allowances means that emission cuts can be achieved at least cost.
The EU ETS is the cornerstone of the EU's strategy for fighting climate change. It is the first international trading system for CO2 emissions in the world and has been in operation since 2005. As of I January 2008 it applies not only to the 27 EU Member States, but also to the other three members of the European Economic Area – Norway, Iceland and Liechtenstein. It currently covers over 10,000 installations in the energy and industrial sectors which are collectively responsible for close to half of the EU's emissions of CO2 and 40% of its total greenhouse gas emissions. An amendment to the EU ETS Directive agreed in July 2008 will bring the aviation sector into the system from 2012.
The EU ETS is a 'cap and trade' system, that is to say it caps the overall level of emissions allowed but, within that limit, allows participants in the system to buy and sell allowances as they require. These allowances are the common trading 'currency' at the heart of the system. One allowance gives the holder the right to emit one tonne of CO2 or the equivalent amount of another greenhouse gas. The cap on the total number of allowances creates scarcity in the market.
In the first and second trading period under the scheme, Member States had to draw up national allocation plans (NAPs) which determine their total level of ETS emissions and how many emission allowances each installation in their country receives. At the end of each year installations must surrender allowances equivalent to their emissions. Companies that keep their emissions below the level of their allowances can sell their excess allowances. Those facing difficulty in keeping their emissions in line with their allowances have a choice between taking measures to reduce their own emissions – such as investing in more efficient technology or using less carbon-intensive energy sources – or buying the extra allowances they need on the market, or a combination of the two. Such choices are likely to be determined by relative costs. In this way, emissions are reduced wherever it is most cost-effective to do so.
The EU ETS was launched on 1 January 2005. The first trading period ran for three years to the end of 2007 and was a 'learning by doing' phase to prepare for the crucial second trading period. The second trading period began on 1 January 2008 and runs for five years until the end of 2012. The importance of the second trading period stems from the fact that it coincides with the first commitment period of the Kyoto Protocol, during which the EU and other industrialised countries must meet their targets to limit or reduce greenhouse gas emissions. For the second trading period EU ETS emissions have been capped at around 6.5% below 2005 levels to help ensure that the EU as a whole, and Member States individually, deliver on their Kyoto commitments.
The EU ETS has put a price on carbon and proved that trading in greenhouse gas emissions works. The first trading period successfully established the free trading of emission allowances across the EU, put in place the necessary infrastructure and developed a dynamic carbon market. The environmental benefit of the first phase may be limited due to excessive allocation of allowances in some Member States and some sectors, due mainly to a reliance on emission projections before verified emissions data became available under the EU ETS. When the publication of verified emissions data for 2005 highlighted this “over-allocation”, the market reacted as would be expected by lowering the market price of allowances. The availability of verified emissions data has allowed the Commission to ensure that the cap on national allocations under the second phase is set at a level that results in real emission reductions.
Besides underlining the need for verified data, experience so far has shown that greater harmonisation within the EU ETS is imperative to ensure that the EU achieves its emissions reductions objectives at least cost and with minimal competitive distortions. The need for more harmonisation is clearest with respect to how the cap on overall emission allowances is set.
The first two trading periods also show that widely differing national methods for allocating allowances to installations threaten fair competition in the internal market. Furthermore, greater harmonisation, clarification and refinement are needed with respect to the scope of the system, the access to credits from emission-reduction projects outside the EU, the conditions for linking the EU ETS to emissions trading systems elsewhere and the monitoring, verification and reporting requirements.
The agreed design changes will apply as of the third trading period, i.e. January 2013. While preparatory work will be initiated immediately, the applicable rules will not change until January 2013 to ensure that regulatory stability is maintained.
The EU ETS in the third period will be a more efficient, more harmonised and fairer system.
Increased efficiency is achieved by means of a longer trading period (8 years instead of 5 years), a robust and annually declining emissions cap (21% reduction in 2020 compared to 2005) and a substantial increase in the amount of auctioning (from less than 4% in phase 2 to more than half in phase 3).
More harmonisation has been agreed in many areas, including with respect to the cap-setting (an EU-wide cap instead of the national caps in phases 1 and 2) and the rules for transitional free allocation.
The fairness of the system has been substantially increased by the move towards EU-wide free allocation rules for industrial installations and by the introduction of a redistribution mechanism that entitles new Member States to auction more allowances.
The climate and energy targets agreed by the 2007 Spring European Council have been maintained and the overall architecture of the Commission's proposal on the EU ETS remains intact. That is to say that there will be one EU-wide cap on the number of emission allowances and this cap will decrease annually along a linear trend line, which will continue beyond the end of the third trading period (2013-2020). The main difference as compared to the proposal is that auctioning of allowances will be phased in more slowly.
In summary, the main changes that have been made to the proposal are as follows:
No. In their NAPs for the first (2005-2007) and the second (2008-2012) trading periods, Member States determined the total quantity of allowances to be issued – the cap – and how these would be allocated to the installations concerned. This approach has generated significant differences in allocation rules, creating an incentive for each Member State to favour its own industry, and has led to great complexity.
As from the third trading period, there will be a single EU-wide cap and allowances will be allocated on the basis of harmonised rules. National allocation plans will therefore not be needed any more.
The rules for calculating the EU-wide cap are as follows:
From 2013, the total number of allowances will decrease annually in a linear manner. The starting point of this line is the average total quantity of allowances (phase 2 cap) to be issued by Member States for the 2008-12 period, adjusted to reflect the broadened scope of the system from 2013 as well as any small installations that Member States have chosen to exclude. The linear factor by which the annual amount shall decrease is 1.74% in relation to the phase 2 cap.
The starting point for determining the linear factor of 1.74% is the 20% overall reduction of greenhouse gases compared to 1990, which is equivalent to a 14% reduction compared to 2005. However, a larger reduction is required of the EU ETS because it is cheaper to reduce emissions in the ETS sectors. The division that minimises overall reduction cost amounts to:
The 21% reduction in 2020 results in an ETS cap in 2020 of a maximum of 1720 million allowances and implies an average phase 3 cap (2013 to 2020) of some 1846 million allowances and a reduction of 11% compared to the phase 2 cap.
All absolute figures indicated correspond to the coverage at the start of the second trading period and therefore don't take account of aviation, which will be added in 2012, and other sectors that will be added in phase 3.
The final figures for the annual emission caps in phase 3 will be determined and published by the Commission by 30 September 2010.
The linear factor of 1.74% used to determine the phase 3 cap will continue to apply beyond the end of the trading period in 2020 and will determine the cap for the fourth trading period (2021 to 2028) and beyond. It may be revised by 2025 at the latest. In fact, significant emission reductions of 60%-80% compared to 1990 will be necessary by 2050 to reach the strategic objective of limiting the global average temperature increase to not more than 2°C above pre-industrial levels.
No, flexibility for installations will not be reduced at all. In any year, the allowances to be auctioned and distributed have to be issued by the competent authorities by 28 February. The last date for operators to surrender allowances is 30 April of the year following the year in which the emissions took place. So operators receive allowances for the current year before they have to surrender allowances to cover their emissions for the previous year. Allowances remain valid throughout the trading period and any surplus allowances can now be "banked" for use in subsequent trading periods. In this respect nothing will change.
The system will remain based on trading periods, but the third trading period will last eight years, from 2013 to 2020, as opposed to five years for the second phase from 2008 to 2012.
For the second trading period Member States generally decided to allocate equal total quantities of allowances for each year. The linear decrease each year from 2013 will correspond better to expected emissions trends over the period.
The tentative annual cap figures are as follows:
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These figures are based on the scope of the ETS as applicable in phase 2 (2008 to 2012), and the Commission's decisions on the national allocation plans for phase 2, amounting to 2083 million tonnes. These figures will be adjusted for several reasons. Firstly, adjustment will be made to take into account the extensions of the scope in phase 2, provided that Member States substantiate and verify their emissions accruing from these extensions. Secondly, adjustment will be made with respect to further extensions of the scope of the ETS in the third trading period. Thirdly, any opt-out of small installations will lead to a corresponding reduction of the cap. Fourthly, the figures do not take account of the inclusion of aviation, nor of emissions from Norway, Iceland and Liechtenstein.
Yes. Industrial installations will receive transitional free allocation. And in those Member States that are eligible for the optional derogation, power plants may, if the Member State so decides, also receive free allowances. It is estimated that at least half of the available allowances as of 2013 will be auctioned.
While the great majority of allowances has been allocated free of charge to installations in the first and second trading periods, the Commission proposed that auctioning of allowances should become the basic principle for allocation. This is because auctioning best ensures the efficiency, transparency and simplicity of the system and creates the greatest incentive for investments in a low-carbon economy. It best complies with the “polluter pays principle” and avoids giving windfall profits to certain sectors that have passed on the notional cost of allowances to their customers despite receiving them for free.
By 31 December 2010, the Commission will adopt EU-wide rules, which will be developed under a committee procedure (“Comitology”). These rules will fully harmonise allocations and thus all firms across the EU with the same or similar activities will be subject to the same rules. The rules will ensure as far as possible that the allocation promotes carbon-efficient technologies. The adopted rules provide that to the extent feasible, allocations are to be based on so-called benchmarks, e.g. a number of allowances per quantity of historical output. Such rules reward operators that have taken early action to reduce greenhouse gases, better reflect the polluter pays principle and give stronger incentives to reduce emissions, as allocations would no longer depend on historical emissions. All allocations are to be determined before the start of the third trading period and no ex-post adjustments will be allowed.
Taking into account their ability to pass on the increased cost of emission allowances, full auctioning is the rule from 2013 onwards for electricity generators. However, Member States who fulfil certain conditions relating to their interconnectivity or their share of fossil fuels in electricity production and GDP per capita in relation to the EU-27 average, have the option to temporarily deviate from this rule with respect to existing power plants. The auctioning rate in 2013 is to be at least 30% in relation to emissions in the first period and has to increase progressively to 100% no later than 2020. If the option is applied, the Member State has to undertake to invest in improving and upgrading of the infrastructure, in clean technologies and in diversification of their energy mix and sources of supply for an amount to the extent possible equal to the market value of the free allocation.
In other sectors, allocations for free will be phased out progressively from 2013, with Member States agreeing to start at 20% auctioning in 2013, increasing to 70% auctioning in 2020 with a view to reaching 100% in 2027. However, an exception will be made for installations in sectors that are found to be exposed to a significant risk of 'carbon leakage'. This risk could occur if the EU ETS increased production costs so much that companies decided to relocate production to areas outside the EU that are not subject to comparable emission constraints. The Commission will determine the sectors concerned by 31 December 2009. To do this, the Commission will assess inter alia whether the direct and indirect additional production costs induced by the implementation of the ETS Directive as a proportion of gross value added exceed 5% and whether the total value of its exports and imports divided by the total value of its turnover and imports exceeds 10%. If the result for either of these criteria exceeds 30%, the sector would also be considered to be exposed to a significant risk of carbon leakage. Installations in these sectors would receive 100% of their share in the annually declining total quantity of allowances for free. The share of these industries' emissions is determined in relation to total ETS emissions in 2005 to 2007.
CO2 costs passed on in electricity prices could also expose certain installations to the risk of carbon leakage. In order to avoid such risk, Member States may grant a compensation with respect to such costs. In the absence of an international agreement on climate change, the Commission has undertaken to modify the Community guidelines on state aid for environmental protection in this respect.
Under an international agreement which ensures that competitors in other parts of the world bear a comparable cost, the risk of carbon leakage may well be negligible. Therefore, by 30 June 2010, the Commission will carry out an in-depth assessment of the situation of energy-intensive industry and the risk of carbon leakage, in the light of the outcome of the international negotiations and also taking into account any binding sectoral agreements that may have been concluded. The report will be accompanied by any proposals considered appropriate. These could potentially include maintaining or adjusting the proportion of allowances received free of charge to industrial installations that are particularly exposed to global competition or including importers of the products concerned in the ETS.
Member States will be responsible for ensuring that the allowances given to them are auctioned. Each Member State has to decide whether it wants to develop its own auctioning infrastructure and platform or whether it wants to cooperate with other Member States to develop regional or EU-wide solutions. The distribution of the auctioning rights to Member States is largely based on emissions in phase 1 of the EU ETS, but a part of the rights will be redistributed from richer Member States to poorer ones to take account of the lower GDP per head and higher prospects for growth and emissions among the latter. It is still the case that 10% of the rights to auction allowances will be redistributed from Member States with high per capita income to those with low per capita income in order to strengthen the financial capacity of the latter to invest in climate friendly technologies. However, a provision has been added for another redistributive mechanism of 2% to take into account Member States which in 2005 had achieved a reduction of at least 20% in greenhouse gas emissions compared with the reference year set by the Kyoto Protocol. Nine Member States benefit from this provision.
Any auctioning must respect the rules of the internal market and must therefore be open to any potential buyer under non-discriminatory conditions. By 30 June 2010, the Commission will adopt a Regulation (through the comitology procedure) that will provide the appropriate rules and conditions for ensuring efficient, coordinated auctions without disturbing the allowance market.
All allowances which are not allocated free of charge will be auctioned. A total of 88% of allowances to be auctioned by each Member State is distributed on the basis of the Member State's share of historic emissions under the EU ETS. For purposes of solidarity and growth, 12% of the total quantity is distributed in a way that takes into account GDP per capita and the achievements under the Kyoto-Protocol.
The ETS covers installations performing specified activities. Since the start it has covered, above certain capacity thresholds, power stations and other combustion plants, oil refineries, coke ovens, iron and steel plants and factories making cement, glass, lime, bricks, ceramics, pulp, paper and board. As for greenhouse gases, it currently only covers carbon dioxide emissions, with the exception of the Netherlands, which has opted in emissions from nitrous oxide.
As from 2013, the scope of the ETS will be extended to also include other sectors and greenhouse gases. CO2 emissions from petrochemicals, ammonia and aluminium will be included, as will N2O emissions from the production of nitric, adipic and glyocalic acid production and perfluorocarbons from the aluminium sector. The capture, transport and geological storage of all greenhouse gas emissions will also be covered. These sectors will receive allowances free of charge according to EU-wide rules, in the same way as other industrial sectors already covered.
As of 2012, aviation will also be included in the EU ETS.
A large number of installations emitting relatively low amounts of CO2 are currently covered by the ETS and concerns have been raised over the cost-effectiveness of their inclusion. As from 2013, Member States will be allowed to remove these installations from the ETS under certain conditions. The installations concerned are those whose reported emissions were lower than 25 000 tonnes of CO2 equivalent in each of the 3 years preceding the year of application. For combustion installations, an additional capacity threshold of 35MW applies. In addition Member States are given the possibility to exclude installations operated by hospitals. The installations may be excluded from the ETS only if they will be covered by measures that will achieve an equivalent contribution to emission reductions.
For the second trading period, Member States allowed their operators to use significant quantities of credits generated by emission-saving projects undertaken in third countries to cover part of their emissions in the same way as they use ETS allowances. The revised Directive extends the rights to use these credits for the third trading period and allows a limited additional quantity to be used in such a way that the overall use of credits is limited to 50% of the EU-wide reductions over the period 2008-2020. For existing installations, and excluding new sectors within the scope, this will represent a total level of access of approximately 1.6 billion credits over the period 2008-2020. In practice, this means that existing operators will be able to use credits up to a minimum of 11% of their allocation during the period 2008-2012, while a top-up is foreseen for operators with the lowest sum of free allocation and allowed use of credits in the 2008-2012 period. New sectors and new entrants in the third trading period will have a guaranteed minimum access of 4.5% of their verified emissions during the period 2013-2020. For the aviation sector, the minimum access will be 1.5%. The precise percentages will be determined through comitology.
These projects must be officially recognised under the Kyoto Protocol’s Joint Implementation (JI) mechanism (covering projects carried out in countries with an emissions reduction target under the Protocol) or Clean Development Mechanism (CDM) (for projects undertaken in developing countries). Credits from JI projects are known as Emission Reduction Units (ERUs) while those from CDM projects are called Certified Emission Reductions (CERs).
On the quality side only credits from project types eligible for use in the EU trading scheme during the period 2008-2012 will be accepted in the period 2013-2020. Furthermore, from 1 January 2013 measures may be applied to restrict the use of specific credits from project types. Such a quality control mechanism is needed to assure the environmental and economic integrity of future project types.
To create greater flexibility, and in the absence of an international agreement being concluded by 31 December 2009, credits could be used in accordance with agreements concluded with third countries. The use of these credits should however not increase the overall number beyond 50% of the required reductions. Such agreements would not be required for new projects that started from 2013 onwards in Least Developed Countries.
Based on a stricter emissions reduction in the context of a satisfactory international agreement, additional access to credits could be allowed, as well as the use of additional types of project credits or other mechanisms created under the international agreement. However, once an international agreement has been reached, from January 2013 onwards only credits from projects in third countries that have ratified the agreement or from additional types of project approved by the Commission will be eligible for use in the Community scheme.
No. Before making its proposal, the Commission analysed the possibility of allowing credits from certain types of land use, land-use change and forestry (‘LULUCF’) projects which absorb carbon from the atmosphere. It concluded that doing so could undermine the environmental integrity of the EU ETS, for the following reasons:
The Commission, the Council and the European Parliament believe that global deforestation can be better addressed through other instruments. For example, using part of the proceeds from auctioning allowances in the EU ETS could generate additional means to invest in LULUCF activities both inside and outside the EU, and may provide a model for future expansion. In this respect the Commission has proposed to set up the Global Forest Carbon Mechanism that would be a performance-based system for financing reductions in deforestation levels in developing countries.
Yes. Projects in EU Member States which reduce greenhouse gas emissions not covered by the ETS could issue credits. These Community projects would need to be managed according to common EU provisions set up by the Commission in order to be tradable throughout the system. Such provisions would be adopted only for projects that cannot be realised through inclusion in the ETS. The provisions will seek to ensure that credits from Community projects do not result in double-counting of emission reductions nor impede other policy measures to reduce emissions not covered by the ETS, and that they are based on simple, easily administered rules.
A stable and predictable regulatory framework is vital for market stability. The revised Directive makes the regulatory framework as predictable as possible in order to boost stability and rule out policy-induced volatility. Important elements in this respect are the determination of the cap on emissions in the Directive well in advance of the start of the trading period, a linear reduction factor for the cap on emissions which continues to apply also beyond 2020 and the extension of the trading period from 5 to 8 years. The sharp fall in the allowance price during the first trading period was due to over-allocation of allowances which could not be “banked” for use in the second trading period. For the second and subsequent trading periods, Member States are obliged to allow the banking of allowances from one period to the next and therefore the end of one trading period is not expected to have any impact on the price.
A new provision will apply as of 2013 in case of excessive price fluctuations in the allowance market. If, for more than six consecutive months, the allowance price is more than three times the average price of allowances during the two preceding years on the European market, the Commission will convene a meeting with Member States. If it is found that the price evolution does not correspond to market fundamentals, the Commission may either allow Member States to bring forward the auctioning of a part of the quantity to be auctioned, or allow them to auction up to 25% of the remaining allowances in the new entrant reserve.
The price of allowances is determined by supply and demand and reflects fundamental factors like economic growth, fuel prices, rainfall and wind (availability of renewable energy) and temperature (demand for heating and cooling) etc. A degree of uncertainty is inevitable for such factors. The markets, however, allow participants to hedge the risks that may result from changes in allowances prices.
Yes. One of the key means to reduce emissions more cost-effectively is to enhance and further develop the global carbon market. The Commission sees the EU ETS as an important building block for the development of a global network of emission trading systems. Linking other national or regional cap-and-trade emissions trading systems to the EU ETS can create a bigger market, potentially lowering the aggregate cost of reducing greenhouse gas emissions. The increased liquidity and reduced price volatility that this would entail would improve the functioning of markets for emission allowances. This may lead to a global network of trading systems in which participants, including legal entities, can buy emission allowances to fulfil their respective reduction commitments.
The EU is keen to work with the new US Administration to build a transatlantic and indeed global carbon market to act as the motor of a concerted international push to combat climate change.
While the original Directive allows for linking the EU ETS with other industrialised countries that have ratified the Kyoto Protocol, the new rules allow for linking with any country or administrative entity (such as a state or group of states under a federal system) which has established a compatible mandatory cap-and-trade system whose design elements would not undermine the environmental integrity of the EU ETS. Where such systems cap absolute emissions, there would be mutual recognition of allowances issued by them and the EU ETS.
Registries are standardised electronic databases ensuring the accurate accounting of the issuance, holding, transfer and cancellation of emission allowances. As a signatory to the Kyoto Protocol in its own right, the Community is also obliged to maintain a registry. This is the Community Registry, which is distinct from the registries of Member States. Allowances issued from 1 January 2013 onwards will be held in the Community registry instead of in national registries.
The Commission will adopt a new Regulation (through the comitology procedure) by 31 December 2011 governing the monitoring and reporting of emissions from the activities listed in Annex I of the Directive. A separate Regulation on the verification of emission reports and the accreditation of verifiers should specify conditions for accreditation, mutual recognition and cancellation of accreditation for verifiers, and for supervision and peer review as appropriate.
Five percent of the total quantity of allowances will be put into a reserve for new installations or airlines that enter the system after 2013 (“new entrants”). The allocations from this reserve should mirror the allocations to corresponding existing installations.
A part of the new entrant reserve, amounting to 300 million allowances, will be made available to support the investments in up to 12 demonstration projects using the carbon capture and storage technology and demonstration projects using innovative renewable energy technologies. There should be a fair geographical distribution of the projects.
In principle, any allowances remaining in the reserve shall be distributed to Member States for auctioning. The distribution key shall take into account the level to which installations in Member States have benefited from this reserve.
The European Parliament's Environment Committee tabled an amendment to the EU ETS Directive requiring allowances in the new entrant reserve to be set aside in order to co-finance up to 12 demonstration projects as requested by the European Council in spring 2007. This amendment has later been extended to include also innovative renewable energy technologies that are not commercially viable yet. Projects shall be selected on the basis of objective and transparent criteria that include requirements for knowledge sharing. Support shall be given from the proceeds of these allowances via Member States and shall be complementary to substantial co-financing by the operator of the installation. No project shall receive support via this mechanism that exceeds 15% of the total number of allowances (i.e. 45 million allowances) available for this purpose. The Member State may choose to co-finance the project as well, but will in any case transfer the market value of the attributed allowances to the operator, who will not receive any allowances.
A total of 300 million allowances will therefore be set aside until 2015 for this purpose.
When an international agreement is reached, the Commission shall submit a report to the European Parliament and the Council assessing the nature of the measures agreed upon in the international agreement and their implications, in particular with respect to the risk of carbon leakage. On the basis of this report, the Commission shall then adopt a legislative proposal amending the present Directive as appropriate.
For the effects on the use of credits from Joint Implementation and Clean Development Mechanism projects, please see the reply to question 20.
Member States have to bring into force the legal instruments necessary to comply with certain provisions of the revised Directive by 31 December 2009. This concerns the collection of duly substantiated and verified emissions data from installations that will only be covered by the EU ETS as from 2013, and the national lists of installations and the allocation to each one. For the remaining provisions, the national laws, regulations and administrative provisions only have to be ready by 31 December 2012.
The Commission has already started the work on implementation. For example, the collection and analysis of data for use in relation to carbon leakage is ongoing (list of sectors due end 2009). Work is also ongoing to prepare the Regulation on timing, administration and other aspects of auctioning (due by June 2010), the harmonised allocation rules (due end 2010) and the two Regulations on monitoring and reporting of emissions and verification of emissions and accreditation of verifiers (due end 2011).