Carbon Offsetting - Market Overview

In order to understand the carbon markets, it is important to recognize the differences between two fundamentally different types of carbon commodities, allowances and offsets, and the systems that create them. The first, allowances, are created by cap-and-trade systems. The second, offsets or carbon credits, are created by baseline-and-credit systems (also sometimes called a project-based system).

Under a cap-and-trade system, an overall cap is set to achieve emissions reductions. Each of the participants within a cap-and-trade system (usually countries, regions or industries) is allocated a certain number of allowances based on an emissions reduction target. In a cap-and-trade system the cap constitutes a finite supply of allowances, set by regulation and political negotiation. These allowances are then neither created nor removed, but merely traded among participants. This finite supply creates a scarcity and drives the demand and price for allowances.

A cap-and-trade system aims to internalize (some of) the costs of emissions, and thus drives actors to seek cost-effective means to reduce their emissions. The challenge in a cap-and-trade programme is to determine the appropriate level at which to set the cap, which should be stringent enough to induce the desired level and rate of change, while minimizing overall economic costs. A baseline-and-credit system in contrast, does not entail a finite supply of allowances. It does not involve projects that are implemented under the umbrella of a cap-and-trade system. Rather, more credits are generated with each new project implemented. These credits can then be used by buyers to comply with a regulatory emission target, to “offset” an emitting activity (such as an airline flight), or to be a “carbon neutral” organisation with zero “net” emissions.

In a baseline-and-credit system a carbon offset buyer can only legitimately claim to offset his emissions if the emissions reductions come from a project that would not have happened anyway. This concept is called additionality in the carbon markets, and refers to the requirement that “[…] reductions in emissions […] are additional to any that would occur in the absence of the certified project activity” (Kyoto Protocol in Article 12.5). Under a cap-and-trade system it is the cap and the allocations rules that drives demand, and determines the level of emissions reduction. Activities that are undertaken in response to the pressure of the cap therefore do not need to prove that they are additional. Additionality is discussed in detail in chapter 5.1.

Cap-and-trade systems often allow for a certain number of offsets to come from emissions reductions that are generated by projects that are not covered under the cap (i.e. from baseline and-credit systems)1. Under a cap-and-trade system the covered sources (for example power producers) have an obligation to reduce their emissions. If these covered sources cannot buy offsets, they will have to reduce their emissions in some other way (e.g. by buying allowances or by increasing efficiency in their plants). If they can buy offsets and these come from projects that are fully additional, then the offsets replace reductions that the cap-and-trade participant would have had to otherwise achieve himself. In other words, under a cap-and-trade system, offsets do not lead to emissions reductions beyond the target set by the cap but only cause a geographical shift in where the emissions reduction occurs. Therefore, non-additional offsets sold into a cap-andtrade system will actually lead to an increase in emissions since the buyer will not have reduced his emissions and the seller will not have offset this increase in emissions.

In a voluntary system, on the other hand, individuals and companies are not required to reduce their emissions. We can therefore assume that they would only do so to a limited extent. The availability of offsets enables them to go beyond what they would have done anyway to reduce their own emissions. The availability of offsets in the voluntary market may therefore lead to additional emissions reduction that would not have happened without the availability of offsets. Buyers in the voluntary market can only claim a unique, incremental “offset“ reduction if the reduction is additional. Yet even without additionality tests, the offset market might induce reductions that would not have happened otherwise, because the market will bring investment to some projects at the margin. But without clearly established additionality, there is no one-to-one correspondence between each credit sold and an additional tonne of reductions.

Distinguishing Features of Cap-and-Trade and Baseline-and-Credit Systems

Features Cap-and-Trade Baseline-and-credit
Exchanged commodity Allowances Carbon Credits
Quantity available Determined by overall cap Generated by each new project
Market dynamic Buyers and sellers have competing and mutually balnaced interests in allowances trades. Buyers and sellers both have an interest in maximizing the offsets generated by a project.
Sources Covered Usually high emitters such as the energy sector and energy intensive industries As defined by each standard. Not limited to just high emitting sectors.
Independent third party Minor role in verifying emissions inventories. Fundamental role in verifying the credibility of the counterfactual baseline and thsu the authenticity ("additionality") of the claimed emission reductions.
Emissions Impact of trade Neutral, as is ensured by zero-sum nature of allowance trades. Neutral, providing projects are additional. Otherwise, net increase in emissions.

Possible decrease in emissions in the voluntary market.

Cap-and-trade systems exist almost exclusively in the compliance market2. Baseline-and-credit systems exist both in the compliance and in the voluntary market. All currently established cap-andtrade programs allow for a limited use of offsets and have an associated offset programme:

Type of Programme Cap-and-Trade Associated Baseline-and-Credit (Offset) Programme
Compliance Market Emissions Trading under Kyoto Protocol CDM & JI
  EU-ETS CDM & JI
  RGGI RGGI Offset Programme
  Western Climate Initiative under development
Voluntary Market Chicago Climate Exchange (CCX) CCX Offset Programme

Except for the CCX Offset Programme, voluntary offset standards are independent of and function outside of a cap-and-trade system3. The following sections provide a brief overview of the compliance and the voluntary markets.

Compliance Market

Carbon markets exist both under compliance schemes and as voluntary programs. Compliance markets are created and regulated by mandatory national, regional or international carbon reduction regimes.

Cap-and-Trade Systems

Emissions Trading Under the Kyoto Protocol

The Kyoto Protocol to the United Nations Framework Convention on Climate Change (UNFCCC) established a cap-and-trade system that imposes national caps on the greenhouse gas emissions of developed countries that have ratified the Protocol (called Annex B countries4). Each participating country is assigned an emissions target and the corresponding number of allowances – called Assigned Amount Units, or AAUs. On average, this cap requires participating countries to reduce their emissions 5.2% below their 1990 baseline between 2008 and 2012. Countries must meet their targets within a designated period of time by:

  • reducing their own emissions; and/or
  • trading emissions allowances with countries that have a surplus of allowances. This ensures that the overall costs of reducing emissions are kept as low as possible; and/or
  • meeting their targets by purchasing carbon credits: to further increase cost-effectiveness of emissions reductions, the Kyoto Protocol also established so-called Flexible Mechanisms: the Clean Development Mechanism (CDM) and Joint Implementation (JI).

European Union Emissions Trading Scheme

The Kyoto Protocol enables a group of several Annex I countries to join together and form a so-called ‘bubble’ that is given an overall emissions cap and is treated as a single entity for compliance purposes. The 15 original member states of the EU formed such a ‘bubble’ and created the EU Emissions Trading Scheme (EU-ETS). The EU-ETS is a company-based cap-and trade system which came into force in 2005. Under this cap-and-trade scheme, emissions are capped and allowances may be traded among countries. The EU-ETS is the largest mandatory cap-and-trade scheme to date. In 2006, it traded 1.1 billion metric tonnes of CO2e, valued at over €16 billion. There are currently several cap-and-trade compliance schemes that operate independently of the Kyoto Protocol. All of these also incorporate a baseline-and-credit component to their programme. Three examples are:

New South Wales GHG Abatement Scheme (NSW GHGAS)

The NSW GHGAS in Australia aims to reduce greenhouse gas emissions from the power sector. It achieves this by using project-based activities to offset the production of greenhouse gas emissions. The programme was established in 2003.

Regional Greenhouse Gas Initiative (RGGI)

RGGI is a multi-state regional cap-and-trade programme for the power sector in the Northeast United States. The RGGI cap-and-trade programme is proposed to start in 2009 and lead to a stabilisation of emissions at current levels (an average of 2002-2004 levels) by 2015, followed by a 10% reduction in emissions between 2015 and 2020. Some of the programme reductions will be achieved outside the electricity sector through emissions offset projects. Offsets serve as the primary cost containment mechanism in RGGI; if allowance prices rise above trigger prices, the ability for regulated sources to use offsets increases.

Western Climate Initiative (WCI)

The WCI is a collaboration of 5 Western US stated and British Columbia launched in early 2007. The initiative set a goal of reducing greenhouse gas emissions by 15% from 2005 levels by 2020 and requires partners to develop a market-based, multi-sector mechanism to help achieve that goal, and participate in a cross-border greenhouse gas (GHG) registry.

Baseline-and-Credit Systems Used within Cap-and-Trade

The Clean Development Mechanism (CDM)

The CDM allows Annex I countries to partly meet their Kyoto targets by financing carbon emission reductions projects in developing countries. Such projects are arguably more costeffective than projects implemented in richer nations because developing countries have on average lower energy efficiencies, lower labor costs, weaker regulatory requirements, and less advanced technologies. The CDM is also meant to deliver sustainable development benefits to the host country. CDM projects generate emissions credits called Certified Emissions Reductions or CERs – one CER is equal to one tonne of carbon dioxide equivalent – which are then bought and traded (see chapter 7.1 for more details on the CDM).

Joint Implementation (JI)

Joint Implementation works similarly to CDM, with the exception that the host country is not a developing nation but another Annex I country. The tradable units from JI projects are called Emissions Reductions Units (ERUs). It is not strictly a baseline-and-credit system since it also has aspects of a cap-and-trade system, and, notably, both participants have an overall reduction target.

The value of both JI and CDM projects has more than doubled in recent years, reaching a combined total of USD 5 billion (EUR 3.9 billion) in 2006 (Capoor & Ambrosi, 2007). Since JI officially starts in 2008, it is not surprising that over 90% of the credits transacted in these markets were produced by CDM projects.

The EU-ETS Linking Directive

The EU Linking Directive, which was passed in 2004, allows operators in phase 2 of the ETS to use credits from Joint Implementation (JI) and the Clean Development Mechanism (CDM) to meet their targets in place of emission cuts within the EU. Member States specify a limit up to which individual installations will be able to use external credits to comply with the ETS. These limits vary between 0% (Estonia) and 22% (Germany) of allowances. There are also restrictions on use of CERs from forestry projects and from certain types of large hydro projects.

Voluntary Carbon Markets

The voluntary carbon markets function outside of the compliance market. They enable businesses, governments, NGOs, and individuals to offset their emissions by purchasing offsets that were created either through CDM or in the voluntary market5. The latter are called VERs (Verified or Voluntary Emissions Reductions). It is noteworthy that about 17% of the offsets sold in the voluntary market in 2006 were sourced from CDM projects (Hamilton, 2007)

Carbon Offsets in the Compliance and in the Voluntary Market

Carbon Offsets in the Compliance and in the Voluntary Market

Unlike under CDM, there are no established rules and regulations for the voluntary carbon market. On the positive side, voluntary markets can serve as a testing field for new procedures, methodologies and technologies that may later be included in regulatory schemes. Voluntary markets allow for experimentation and innovation because projects can be implemented with fewer transaction costs than CDM or other compliance market projects. Voluntary markets also serve as a niche for micro projects that are too small to warrant the administrative burden of CDM6 or for projects currently not covered under compliance schemes. On the negative side, the lack of quality control has led to the production of some low quality VERs, such as those generated from projects that appear likely to have happened anyway (see chapter 5.1 on additionality.)

Voluntary and Compliance Carbon Market Size

Compared to the compliance market, trading volumes in the voluntary market are much smaller because demand is created only by voluntary wish to buy offsets whereas in a compliance market, demand is created by a regulatory instrument. Because there is much lower demand, because quality standards are not widely established, and because they are not fungible in compliance markets, carbon offsets sold in the voluntary market tend to be cheaper than those sold in the compliance market

Offset Trading Volumes in the Kyoto and in the Voluntary Markets

In 2006, 23 million tonnes of CO2e were traded at a value of €62.6 million (Hamilton, 2007) in the voluntary market – the trading value of the compliance market, including allowances and credits was €23 billion in 2006. The value of CDM and JI credits was €3.8 billion in 2006. (Capoor and & Ambrosi, 2007.) Nevertheless, the voluntary carbon market has grown dramatically over the last couple of years. According to a recent report, the voluntary offset market grew 200% between 2005 and 2006 (Hamilton, 2007).

1 For example, the EU-ETS allows for CDM credits (CERs) to be used interchangeably with their allowances (EUAs). In the case of the EU-ETS, it is the countries themselves who set the limit on what percentage of CERs are allowed into their system. Allowing CERs will de-facto increase the number of available allowances and therefore raises the cap. On the other hand, it makes achieving reductions potentially more cost effective.
2 An exception to this is the Chicago Climate Exchange which is a voluntary but legally binding cap-and-trade regime.
3 Although the Gold Standard also certifies CDM credits, it is a voluntary standard.
4 Annex 1 or Annex B?
In practice, Annex 1 of the UNFCCC Convention and Annex B of the Kyoto Protocol are used almost interchangeably. However, strictly speaking, it is the Annex 1 countries that can invest in JI / CDM projects as well as host JI projects, and non-Annex 1 countries that can host CDM projects, even though it is the Annex B countries that have the emission reduction obligations under the Protocol. Note that Belorus and Turkey are listed in Annex 1 but not Annex B; and that Croatia, Liechtenstein, Monaco and Slovenia are listed in Annex B but not Annex 1. (source: www.cdmcapacity.org/glossary.html)
5 When compliance market credits are used for voluntary offsetting, they are retired, thus do not go towards assisting or meeting any legally-binding reduction targets.
6 According to project developers, carbon offset project must reduce at least 5,000 metric tonnes of CO2 per year in order justify the CDM transaction costs. (myclimate, personal communication.)

Published by: WWF Germany

Title: Making Sense of the Voluntary Carbon Market: A Comparison of Carbon Offset Standards

Authors: Anja Kollmuss (SEI-US), Helge Zink (Tricorona), Clifford Polycarp (SEI-US)

Graphic Design: Tyler Kemp-Benedict

Date: March 2008