|European Union Emissions Trading System (EU ETS)|
|European Union Carbon Market Glossary|
European Union Emissions Trading System (EU ETS) is the cornerstone of the European Union's policy to tackle climate change and its key tool for cost-effective reduction of emissions of carbon dioxide (CO2) and other greenhouse gases (GHG) in the power, aviation and industrial sectors.
The EU ETS was launched in 2005 and is the first - and still by far the largest - international system for trading greenhouse gas emission allowances covering over three-quarters of the allowances traded on the international carbon market.
The EU ETS operates in the 31 countries of the European Economic Area (EEA).
It limits emissions from nearly 11,000 power plants and manufacturing installations as well as slightly over 500 aircraft operators flying between EEA's airports (Report from the Commission to the European Parliament and to the Council, Report on the functioning of the European carbon market, 23 November 2017 (COM(2017) 693 final, p. 7).
From the start of phase 3 (2013 - 2020), the system covers around 45% of the EU's GHG emissions.
EU Member States may add more sectors and greenhouse gas emissions to the EU ETS (opt-in procedure).
The EU ETS works on the 'cap and trade' principle and is a market-based measure where participants are required to monitor and report their emissions and surrender sufficient emission allowances to cover their reported emissions in each year.
Emission allowances can be traded to enable abatement to occur where it is most cost effective to do, thereby lowering the overall cost of tackling climate change.
The EU ETS was designed as a quantitative instrument in which a predetermined quantity of emission allowances is released to reach the desired environmental aim, which, under Article 1 of the EU ETS Directive, is ‘to promote reductions of greenhouse gas emissions in a cost-effective and economically efficient manner’ (European Court of Justice in the judgment of 21 June 2018, Republic of Poland v European Parliament and Council of the European Union, Case C-5/16).
European Court of Justice assessed in the said judgment of 21 June 2018 that the system “does not intervene directly to set the price of allowances, the latter being determined exclusively by market forces, on the basis of, inter alia, the scarcity of allowances, combined with the flexibility provided by the possibility of trading allowances.”
The price signal created at EU level is supposed to influence the operational and strategic decisions of investors.
EU ETS cap
A 'cap' is an absolute quantity of greenhouse gases which can be emitted by the factories, power plants and other installations in the system, to ensure the emission reduction target is met.
The cap corresponds to number of allowances put in circulation over a trading phase (period).
In phases 1 and 2 (2005 - 2012) the EU-wide cap was determined in a bottom-up manner from the aggregated total quantity of allowances laid down by Member States in their National Allocation Plans (NAPs).
As from the start of the phase 3, an EU-wide cap is determined by the EU ETS Directive.
The 2013 cap for emissions from stationary installations was set at 2 084 301 856 allowances.
This cap decreases each year by a linear reduction factor of 1.74% of the average total quantity of allowances issued annually in 2008-2012, thus ensuring that the number of allowances that can be used by stationary installations will be 21% lower in 2020 than in 2005.
The inherent assumptions are that in 2020, emissions from sectors covered by the EU ETS will be 21% lower than in 2005 and by 2030 the decrease will reach the level of 43%.
EU ETS annual cap for installations for the years 2013-2020 was as follows (source: Report from the Commission to the European Parliament and to the Council, Report on the functioning of the European carbon market, 23 November 2017 (COM(2017) 693 final, p. 11):
- 2013 - 2 084 301 856,
- 2014 - 2 046 037 610,
- 2015 - 2 007 773 364,
- 2016 - 1 969 509 118,
- 2017 - 1 931 244 873,
- 2018 - 1 892 980 627,
- 2019 - 1 854 716 381,
- 2020 - 1 816 452 135.
Improvements of the EU ETS in the third phase
A major revision of the EU ETS system was agreed in 2009, for the implementation in the third trading phase to run from 2013 until 2020.
The overall driver for the 2009 EU ETS reform was to streamline its operating rules through increased harmonisation of its pre-existing parts fragmented by national borders of the EU Member States.
This tendency has been expressed, in particular, in the following EU ETS features in the period 2013-2020:
- For the purposes of enhanced predictability and stability, a single, EU-wide cap on has been imposed na the allowances' volume, the cap is decreasing by 1.74% annually (in line with the Linear Reduction Factor - LRF), and replaces the previous system of the EU Member States' national caps;
- Open, transparent, harmonised and non-discriminatory auctioning has replaced the free allocation as the default method for allocating emission allowances (the detailed rules are stipulated in the EU ETS Auctioning Regulation;
- The procedures for the free allocation of emission allowances have also been harmonised across the EU and ambitious EU-wide ex-ante performance benchmarks have been introduced (Benchmarking Decision);
- Regulation for monitoring and reporting and Regulation for verification of emission reports and accreditation and supervision of verifiers have been adopted and apply directly in all EU Member States;
- Stricter rules and conditions for the use of international carbon credits in the EU ETS with harmonised limits for their use by operators (for details see here);
- Central electronic Union Registry has replaced the emissions allowances registries run previously individually by the EU Member States. The Central Union Emissions Allowances Registry is governed by a Registry Regulation applying directly in all EU Member States.
Another reform under implementation is to change the emission allowances legal status into financial instruments and subject them (along with being already in scope derivative financial instruments or auctioned products based on them) to financial market supervisory system, mainly to the Markets in Financial Instruments Directive and Regulation under the MiFID II package and the Market Abuse Regulation.
The European Commission in November 2012 proposed a short-term measure to postpone (back-load) auctioning of 900 million emission allowances until 2019 and 2020. The European Parliament and the Council agreed on the proposal in December 2013 and the implementation of back-loading started in March 2014 (more on the EU ETS allowances backloading read here).
Subsequently, in January 2014 a proposal to establish a Market Stability Reserve was presented (the legislative process has been finalised with the adoption of the Decision (EU) 2015/1814 of the European Parliament and of the Council of 6 October 2015 concerning the establishment and operation of a market stability reserve for the Union greenhouse gas emission trading scheme and amending Directive 2003/87/EC).
On 15 July 2015 the Commission presented a legislative proposal to revise the EU Emissions Trading System in line with the 2030 framework.
Coverage of activities, installations and aircraft operators
In terms of greenhouse gases EU ETS scope was firstly defined in the Directive 2003/87/EC and has been amended by the Directive 2009/29/EC, including some new activities (such as production and processing of non-ferrous metals, some chemicals etc.) and new greenhouse gases (nitrous oxide (N2O) and perfluorocarbons (PFCs)).
The EU ETS currently covers carbon dioxide (CO2) emissions, nitrous oxide (N2O) emissions from all nitric, adipic, glyoxal and glyoxylic acid production and perfluorocarbons (PFC) emissions from aluminium production (see Annex I of the Directive which lists the categories of activities to which the ETS currently applies).
As from the start of the phase 3 of the EU ETS (i.e. 1 January 2013), the sectors with stationary installations covered by the EU ETS are energy intensive industries, including power stations and other combustion plants, with ≥20MW thermal rated input (except hazardous or municipal waste installations), oil refineries, coke ovens, iron and steel, cement clinker, glass, lime, bricks, ceramics, pulp, paper and board, aluminium, petrochemicals, ammonia, nitric, adipic, glyoxal and glyoxylic acid production, CO2 capture, transport in pipelines and geological storage of CO2.
Even though participation in the EU ETS is mandatory, in some sectors only installations above a certain size are included.
Moreover, participating countries can exclude small installations from the system if measures are in place that will cut their emissions by an amount equivalent to the amount of emissions which would have been cut had the installations been included in the EU ETS.
Participating countries may also add more sectors and GHGs to the EU ETS.
The EU ETS covers about 11 000 power plants and manufacturing installations in all EU Member States, Iceland, Norway and Liechtenstein (Report on the functioning of the European carbon market, accompanying the document Report from the Commission to the European Parliament and to the Council, Climate action progress report, including the report on the functioning of the European carbon market and the report on the review of Directive 2009/31/EC on the geological storage of carbon dioxide of 18 November 2015 (COM(2015) 576 final), p. 5).
The aviation scope of the EU ETS is limited to flights within the EEA until 2016.
The aviation activities within the initial scope of the EU ETS included all flights from or to an aerodrome situated in the territory of a Member State to which the Treaty applies, with some exceptions as listed in Annex I of the EU ETS Directive.
However, in the light of the negotiations within ICAO looking to propose a global market based mechanism for reduction of aviation emissions, this scope has been temporarily reduced and only flights within the EEA are covered.
Table: Key features of the EU ETS across trading phases
Source of the Table: EU ETS Handbook, p. 18, 19
There are four types of tradable credits under the EU ETS:
EUAs are most common units, EUAAs entitle the holder to emit one tonne of carbon dioxide within the valid period, has been created specifically for the compliance of aircraft operators and can be surrendered only by aviation operators and enjoy considerably smaller tradable demand.
Qualifying credits for emission reductions accomplished outside the European Union, which can be also, within certain limits, submitted for compliance under EU ETS are CERs and ERUs (however, they need to be translated into EUAs in order to count for compliance purposes).
CERs are obtained through the Clean Development Mechanism (CDM), which allows emission reductions achieved in less developed country to be credited in a developed country.
ERUs are produced through the Joint Implementation (JI) mechanism, which promotes technology transfer between Kyoto Protocol Annex 1 countries.
EU ETS carbon market
The EU ETS carbon market is dominated by derivatives - it is assessed around 85% of trade in allowances involves the use of derivatives: futures, forwards, options, which are subject to EU financial markets regulations.
In 2014, the EU ETS total volume traded was 8.33 billion tonnes of CO2 either as spot allowances or derivatives of allowances (total value of EUR 47 billion), where only around 900 million allowances were traded on the spot market (value of about EUR 5.2 billion).
EU ETS covers more than 11 000 power stations and industrial plants in 31 countries, around 2 000 intermediaries, traders, organisations and individuals voluntarily participate in the EU ETS.
|Last Updated on Friday, 04 January 2019 13:45|