This Annex provides the main assumptions for the modelling of ETS coverage and free allowance shares. It also details the data sources for ETS-covered emissions, free allowances and permit prices.
Effective Carbon Rates 2025
Annexe B. Data sources and methodology for Emissions Trading Systems modelling
Copy link to Annexe B. Data sources and methodology for Emissions Trading Systems modellingGeneral methodology: Permit prices, coverage and free allowance shares
Copy link to General methodology: Permit prices, coverage and free allowance sharesPermit prices
Permit prices are calculated as the average auction prices (primary market prices) across the year under consideration (e.g. 2023 for ECR 2023), if the data is available. The average is taken to smooth price fluctuations, as permit prices experience volatility throughout the year. For some emissions trading systems, price information is only available for part of the year, in which case an average across the available dates is calculated, or for a single auction or date, in which case this price is used. Due to data availability, secondary market prices rather than auction prices are used in the calculation for certain systems.
Coverage
For most systems, ETS coverage is estimated by reference to verified emissions data at facility level or at aggregated facility level (e.g. firm). This emission data is then matched where possible at a subsector-level, and if not at a sector-level (e.g. using ISIC classification). Where this data is not available, broader measures are used such as the total emissions covered or the share of sectoral emissions covered. Data availability and sources are exposed below. It is not possible however, to distinguish coverage by fuels: the implicit assumption is thus that at the subsector level, the composition of fuel use is the same for ETS-covered entities and entities not subject to an ETS.
Free allowance shares
Where verified emissions data is available, it may be the case that free allowance data also is (see below, Table A B.1). In this case, the share of freely allocated allowances in total verified emissions is calculated at the subsector and sector level according to the following formula (where i is an entity, FA are the free allowances and VE are the verified emissions):
If no free allowance data is available, other methodologies are used, e.g. relying on the quantity of allowances auctioned or the free allowance allocation formula. The share may generally then only be calculated at the system-level and used as an approximation for sector-level shares (if many sectors are covered by the ETS).
In a few cases, free allowances are modelled as decreasing the share of emissions covered or as not impacting the average price signal (i.e. the EACR). If free allowances are not tradable but may be used for compliance, then this is modelled as decreasing the share of emissions effectively covered. If free allowances are adjusted ex-post to equal verified emissions, then this is also modelled as decreasing emissions effectively covered (in effect, this is modelled as equivalent to reporting emissions without pricing them). In both of these cases, the free allowance allocation rules do not maintain the marginal price signal: there is no opportunity cost of emitting as much as the free allowance allocation received. If free allowances should be consigned to auctions and their revenues used for programs to reduce GHG emissions or to return to ratepayers as non-volumetric credits (as in the California Cap-and-Trade Program and in the Washington Cap-and-Invest Program), then these are modelled as not affecting EACRs (consistent with Flues and Van Dender (2017[12])). Table A B.3 presents more details on free allowance allocation methods.
Country-level data sources and information
Copy link to Country-level data sources and informationThis report covers 34 ETSs in 2023 and this section provides information on the sources and information used for the modelling of these ETSs in 2023. It starts by presenting the data source used for permit prices in each ETS, the availability or not of verified emissions data (and if not available the alternative sources used for the modelling of ETS coverage) and of free allowance allocation data (Table A B.1). It also presents the sectors covered by each ETS (according to the CPET classification of sectors – see Table A A.1) and the greenhouse gases covered (Table A B.2). Finally, it also presents the free allowance allocation methods in each system (Table A B.3)
The following table presents free allowance allocation methods across the 34 ETSs analysed in this report, and takes note of instances where additional restrictions or flexibilities apply. In particular, it highlights where traditional benchmarking methods are complemented with considerations accounting for changes in production.
Table A B.1. Sources for permit prices, verified emissions and free allowance amounts
Copy link to Table A B.1. Sources for permit prices, verified emissions and free allowance amounts34 ETSs, 2023
|
System |
Permit Price |
Verified Emissions |
Free allowances |
||
|---|---|---|---|---|---|
|
Source |
Primary or secondary market |
Source |
Level of information*** |
Source |
|
|
Australia Safeguard Mechanism |
Safeguard Mechanism default prescribed unit price for 2023-24 (https://www.dcceew.gov.au/climate-change/emissions-reporting/national-greenhouse-energy-reporting-scheme/safeguard-mechanism#toc_8) |
Secondary |
Clean Energy Regulator website |
Entity-level |
Clean Energy Regulator website |
|
Austrian ETS |
Legislation (https://www.bmf.gv.at/themen/klimapolitik/carbon-markets/nationales-emissionszertifikatehandelsgesetz-2022-(NEHG-2022)/entwicklung-und-handelsphasen.html) |
Primary |
Data provided by the Austrian Ministry of Finance |
Total |
n.a. |
|
Canada - Alberta |
ICAP (factsheet), as accessed in January 2025. |
Primary |
Alberta Government website |
Sector-level |
Alberta Government website |
|
Canada - New Brunswick |
ICAP (factsheet), as accessed in January 2025. |
Primary |
Modelled using information in ICAP (2025) |
Total |
Modelled |
|
Canada - Newfoundland and Labrador |
ECCC (2021), Update to the Pan-Canadian Approach to Carbon Pollution Pricing 2023-2030 |
Primary |
Newfoundland and Labrador Department of Environment and Climate Change |
Entity-level |
Modelled |
|
Canada - Nova Scotia |
ICAP (factsheet), as accessed in January 2025. |
Primary |
Modelled by matching the list of regulated facilities (Climate Change in Nova Scotia website) with emissions data from the GHG Reporting Program (GHGRP) |
Entity-level |
Modelled |
|
Canada - Ontario |
ECCC (2021), Update to the Pan-Canadian Approach to Carbon Pollution Pricing 2023-2030 |
Primary |
Ministry of the Environment, Conservation and Park website |
Entity-level |
Modelled |
|
Canada - Québec |
ICAP Allowance Price Explorer (retrieved from the Ministry for the Fight Against Climate Change website) |
Primary |
Québec Ministère de l’Environnement, de la Lutte contre les changements climatiques, de la Faune et des Parcs website |
Entity-level |
Data provided by Direction du marché du carbone |
|
Canada - Saskatchewan |
ECCC (2021), Update to the Pan-Canadian Approach to Carbon Pollution Pricing 2023-2030 |
Primary |
Modelled using information in ICAP (2025) |
Total |
Modelled |
|
Canada FOBPS * |
ECCC (2021), Update to the Pan-Canadian Approach to Carbon Pollution Pricing 2023-2030 |
Primary |
Modelled using coverage shares from the Pan-Canadian Approach to Pricing Carbon Pollution report combined with the latest provincial GHG inventories |
Total |
Modelled |
|
China - Beijing |
ICAP Allowance Price Explorer (retrieved from the China Beijing Environmental Exchange) |
Primary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China - Chongqing |
ICAP Allowance Price Explorer (retrieved from the Chongqing Carbon Emissions Trading Centre) |
Secondary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China - Fujian |
ICAP Allowance Price Explorer (retrieved from the Haixia Equity Exchange) |
Secondary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China - Guangdong |
ICAP Allowance Price Explorer (retrieved from the China Emissions Exchange (Guangzhou)) |
Secondary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China - Hubei |
ICAP Allowance Price Explorer (retrieved from the China Hubei Emission Exchange) |
Primary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China - Shanghai |
ICAP Allowance Price Explorer (retrieved from the Shanghai Environmental and Energy Exchange) |
Primary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China - Shenzhen |
ICAP Allowance Price Explorer (retrieved from the China Emissions Exchange (Shenzhen)) |
Secondary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China - Tianjin |
ICAP Allowance Price Explorer (retrieved from the Tianjin Climate Exchange) |
Secondary |
Modelled based on ECR (2016), updated using changes in regulation and list of covered entities |
Total |
Modelled |
|
China national ETS |
ICAP Allowance Price Explorer (retrieved from the Shanghai Environmental and Energy Exchange) |
Secondary |
Modelled using legislation |
Total |
Modelled |
|
EU ETS |
ICAP Allowance Price Explorer (EUA auction price and revenue data provided by the EEX Group) |
Primary |
European Union Registry |
Entity-level |
European Union Registry |
|
German ETS |
Legislation (https://www.bundesumweltministerium.de/en/law/fuel-emissions-trading-act) |
Primary |
German Emissions Trading Authority ( DEHSt ) website |
Total |
n.a. |
|
Indonesia ETS |
ICAP Status Report (2025) |
Secondary |
Data provided by the Ministry of Energy and Mineral Resources |
Total |
Modelled |
|
Japan - Saitama |
Tokyo Metropolitan Government (https://www.kankyo.metro.tokyo.lg.jp/documents/d/kankyo/2024_05) |
Secondary |
Saitama Prefecture website |
Total |
Modelled |
|
Japan -Tokyo |
Tokyo Metropolitan Government (https://www.kankyo.metro.tokyo.lg.jp/documents/d/kankyo/2024_05) |
Secondary |
Tokyo Metropolitan Government website |
Total |
Modelled |
|
Kazakhstan ETS |
ICAP Status Report (2025) |
Secondary |
Modelled using information in ICAP (2025) |
Total |
National Carbon Quota Plan for 2022-2025 |
|
Korea ETS |
ICAP Allowance Price Explorer (retrieved from the Korea Exchange) |
Secondary |
Emissions Trading Registry System, Greenhouse Gas inventory and Research Center of Korea (GIR) website |
Entity-level |
Emissions Trading Registry System, Greenhouse Gas inventory and Research Center of Korea (GIR) website |
|
Mexico ETS |
n.a. |
n.a. |
Modelled using information in ICAP (2025) |
Total |
n.a. |
|
New Zealand ETS |
ICAP Allowance Price Explorer (supplied by Jarden) |
Secondary |
New Zealand Environmental Protection Authority (EPA) website |
Entity-level |
New Zealand Environmental Protection Authority (EPA) website |
|
Swiss ETS |
ICAP Allowance Price Explorer (retrieved from the Swiss Emissions Registry) |
Primary |
Swiss emissions registry (stationary sources), Federal Office for the Environment FOEN website (aviation) |
Entity-level |
Swiss emissions registry (stationary sources), Federal Office for the Environment FOEN website (aviation) |
|
UK ETS |
ICAP Allowance Price Explorer (retrieved from the Intercontinental Exchange (ICE) platform)(1) |
Primary |
UK Emissions Trading Registry(2) |
Entity-level |
UK Emissions Trading Registry1 |
|
United States - California |
ICAP Allowance Price Explorer (retrieved from the Air Resources Board website) |
Primary |
Californian Air Resource Board (ARB) website |
Entity-level |
|
|
United States - Massachusetts |
Massachusetts auction reports (https://www.mass.gov/lists/massachusetts-carbon-allowance-registry-document-repository) |
Primary |
Modelled using RGGI information |
Entity-level |
n.a. |
|
United States - RGGI ** |
ICAP Allowance Price Explorer (retrieved from the RGGI website) |
Primary |
RGGI CO2 Allowance Tracking System (RGGI COATS) |
Entity-level |
n.a. |
|
United States - Washington |
ICAP Allowance Price Explorer (end-of-day and weekly average data is provided by ICE)(1) |
Primary |
Department of Ecology, State of Washington website |
Entity-level |
Clean Energy Regulator website |
Note: * Over the course of 2023, the federal OBPS was operational in Manitoba, Nunavut, Prince Edward Island and Yukon.
** RGGI (Regional Greenhouse Gas Initiative): in 2023, it operates with ten the states of Connecticut, Delaware, Maine, Maryland, Massachusetts, New Hampshire, New Jersey, New York, Rhode Island, Vermont and Virginia.
*** Depending on the system, the term “entity” is used to refer to installations, firms, aviation operators or fuel distributors.
n.a.: not available or not applicable.
(1) Disclaimer on use or reference to ICE Data: intercontinental exchange, inc., ice data llp, and/or any of its affiliates (“ice group”), makes no warranty, express or implied, either as to the results to be obtained from the use of ice futures data and/or the figure at which ice futures data stands at any particular time on any particular day or otherwise. The use of ice futures data is provided on an ‘as is’ basis and ice group disclaims all liability for any loss or damage whatsoever incurred by the use of ice futures data herein, even if ice group has been advised of the possibility of such losses, damages or expenses. Any distribution or commercial use of ice futures data is prohibited without the prior written consent of ice data llp.
(2) Complemented by European Union Registry for Northern Ireland power plants still under the EU ETS.
Source: ICAP (2025[13]) and Authors.
The following table presents coverage of sectors (according to the CPET classification) and GHGs by ETS. Coverage can in some cases be minimal and does not indicate that the whole of the sector’s emissions are covered.
Table A B.2. Sectors and GHGs covered by ETSs
Copy link to Table A B.2. Sectors and GHGs covered by ETSs34 ETSs, 2023
|
System |
CPET sectors |
"Other GHGs" covered |
GHG emissions |
|---|---|---|---|
|
Australia Safeguard Mechanism |
Buildings, Electricity, Industry, Off-road and Road transport (point source) |
Yes |
CO2 from energy use and from industrial processes; CH4 from energy use, from industrial processes, from fugitive emissions and from waste treatment, disposal and remediation and wastewater handling; N2O from energy use, from industrial processes and from wastewater handling; F-gases from industrial processes |
|
Austrian ETS |
Agriculture and fisheries, Buildings, Industry, Off-road and Road transport (upstream) |
Yes |
CO2, CH4 and N2O from energy use |
|
Canada - Alberta |
Electricity, Industry (point source) |
Yes |
CO2, CH₄, N₂O, NF3, SF₆, HFCs, PFCs from energy extraction and use and from industrial processes |
|
Canada - New Brunswick |
Electricity, Industry (point source) |
Yes |
CO2, CH₄, N₂O, NF3, SF₆, HFCs, PFCs from energy extraction and use and from industrial processes |
|
Canada - Newfoundland and Labrador |
Electricity, Industry (point source) |
Yes |
CO2, CH₄, N₂O, NF3, SF₆, HFCs, PFCs from energy extraction and use and from industrial processes |
|
Canada - Nova Scotia |
Electricity, Industry (point source) |
Yes |
CO2, CH₄, N₂O, SF₆, HFCs, PFCs from energy use and industrial processes |
|
Canada - Ontario |
Electricity, Industry (point source) |
Yes |
CO2, CH₄, N₂O, SF₆, HFCs, PFCs from energy use and industrial processes |
|
Canada - Québec |
Electricity (point source and downstream), Buildings, Industry, Off-road transport (point source and upstream), Agriculture and fisheries and Off-road and Road transport (upstream) |
Yes |
CO2, CH₄, N₂O, NF3, SF₆, HFCs, PFCs from energy use and industrial processes |
|
Canada - Saskatchewan |
Electricity, Industry (point source) |
Yes |
CO2, CH₄, N₂O, NF3, SF₆, HFCs, PFCs from energy extraction and use and from industrial processes |
|
Canada FOBPS * |
Electricity, Industry (point source) |
Yes |
CO2, CH₄, N₂O, SF₆, HFCs, PFCs from energy use and industrial processes |
|
China - Beijing |
Buildings, Industry, Road transport (point source)(1),(2) |
Yes |
CO2 from energy use and from industrial processes |
|
China - Chongqing |
Industry (point source)(1),(2) |
Yes |
CO2, CH4, N₂O, HFCs, PFCs, SF6 from energy use and from industrial processes |
|
China - Fujian |
Industry, Offroad transport (point source)(1),(2) |
Yes |
CO2 from energy use and from industrial processes |
|
China - Guangdong |
Buildings, Industry, Off-road transport (point source)(1),(2) |
Yes |
CO2 from energy use and from industrial processes |
|
China - Hubei |
Buildings, Industry (point source) (1),(2) |
Yes |
CO2 from energy use and from industrial processes |
|
China - Shanghai |
Buildings, Industry, Off-road transport (point source) (1),(2) |
Yes |
CO2 from energy use and from industrial processes |
|
China - Shenzhen |
Buildings, Industry, Off-road and Road transport (point source) (1),(2) |
Yes |
CO2 from energy use and from industrial processes |
|
China - Tianjin |
Buildings, Industry (point source) (1),(2) |
Yes |
CO2 from energy use and from industrial processes |
|
China national ETS |
Electricity(3) |
Yes |
CO2 (from energy use) |
|
EU ETS |
Agriculture and fisheries,(4) Buildings,(4) Electricity, Industry, Off-road transport (point source) |
Yes |
CO2 from energy use, CO2 from industrial processes, N2O from adipic acid, nitric acid and glyoxylic acid production, PFCs from aluminium production |
|
German ETS |
Agriculture and fisheries, Buildings, Industry, Off-road and Road transport (upstream) |
No |
CO2 (from energy use) |
|
Indonesia ETS |
Electricity (point source) |
Yes |
CO2, N2O and CH4 (from energy use) |
|
Japan - Saitama |
Buildings, Industry (point source), Electricity (downstream) |
No |
CO2 from energy use |
|
Japan -Tokyo |
Buildings, Industry (point source), Electricity (downstream) |
No |
CO2 from energy use |
|
Kazakhstan ETS |
Electricity, Industry (point source) |
Yes |
CO2 emissions from energy use and industrial processes |
|
Korea ETS |
Buildings, Electricity, Industry, Off-road and road transport (point source), Electricity and Heat (downstream) |
Yes |
CO₂, CH4, N₂O, HFCs, PFCs, SF6 from energy use and industrial processes |
|
Mexico ETS |
Electricity, Industry (point source) |
Yes |
CO2 from energy use and industrial processes |
|
New Zealand ETS |
All CPET sectors (upstream for all energy-related emissions, as fuel distributors are covered, and point source for sectors such as industry and waste) |
Yes |
CO2, CH₄, N₂O from energy, waste and industrial processes and SF₆, HFCs, PFCs from industrial processes. |
|
Swiss ETS |
Electricity, Industry, Off-road transport (point source) |
Yes |
CO2 from energy use and industrial processes; N2O, CH4 and F-gases from industrial processes |
|
UK ETS |
Buildings,(5) Electricity, Industry, Off-road transport (point source) |
Yes |
CO2 from energy use, CO2 from industrial processes, N2O from adipic acid, nitric acid and glyoxylic acid production, PFCs from aluminium production |
|
United States - California |
Electricity (point source and downstream), Buildings, Industry, Off-road transport (point source and upstream), Agriculture and fisheries and Off-road and Road transport (upstream) |
Yes |
CO2, CH4, N2O from energy use and industrial processes |
|
United States - Massachusetts |
Electricity (point source) |
No |
CO2 (from energy use) |
|
United States - RGGI ** |
Electricity (point source) |
No |
CO2 (from energy use) |
|
United States - Washington |
Electricity (point source), Buildings, Industry, Off-road transport (point source and upstream), Off-road and Road transport (upstream) |
Yes |
CO2, CH4, N2O from energy and industrial processes, HFCs, PFCs, SF6, NF3, other fluorinated GHGs from industrial processes |
Note: * Over the course of 2023, the federal OBPS was operational in Manitoba, Nunavut, Prince Edward Island and Yukon.
** RGGI (Regional Greenhouse Gas Initiative): in 2023, it operates with ten the states of Connecticut, Delaware, Maine, Maryland, Massachusetts, New Hampshire, New Jersey, New York, Rhode Island, Vermont and Virginia.
(1) Due to data limitations or negligeable estimated coverage, the coverage methodology only applies only to: (i) Industry for Chongqing, Fujian, Hubei, Shenzhen and Tianjin; (ii) Industry and buildings for Beijing, Guangdong and Shanghai.
(2) Sold heat and electricity may also be covered downstream in Chinese Pilot ETSs.
(3) The Chinese national ETS may also cover certain electricity autoproduction installations, though not modelled here.
(4) Agricuture and fisheries as well as Buildings (commercial and public services installations) are covered through stationary combustion (with >20 MW thermal rated input). This does not refer to upstream system that would cover fuels used in these sectors. In the majority of countries covered by the EU ETS, this concerns less than 10 installations.
(5) This refers to the coverage of certain commercial and public services installations’ emissions at point source (combustion of fuels in
installations with a total rated thermal input exceeding 20 MW) and this coverage represents a limited share of emissions in the UK buildings sector (less than 1% of the sector’s emissions in the UK). This does not refer to upstream system that would cover fuels used in the buildings sector.
Source: ICAP (2025[13]) and Authors.
The following table presents free allowance allocation methods across the 34 ETSs analysed in this report, and takes note of instances where additional restrictions or flexibilities apply. In particular, it highlights where traditional benchmarking methods are complemented with considerations accounting for changes in production.
Table A B.3. Free allowance allocation methods in ETSs
Copy link to Table A B.3. Free allowance allocation methods in ETSs34 ETSs, 2023
|
System |
Method |
Note |
|---|---|---|
|
Australia Safeguard Mechanism |
output-based benchmarking |
Unless the baseline is of less than 100,000 tCO₂e (in which case a default of 100,000 tCO₂e is applied). |
|
Austrian ETS |
n.a. |
|
|
Canada - Alberta |
output-based benchmarking |
|
|
Canada - New Brunswick |
output-based benchmarking |
|
|
Canada - Newfoundland and Labrador |
output-based benchmarking |
|
|
Canada - Nova Scotia |
output-based benchmarking |
|
|
Canada - Ontario |
output-based benchmarking |
|
|
Canada - Québec |
benchmarking |
|
|
Canada - Saskatchewan |
output-based benchmarking |
|
|
Canada FOBPS * |
output-based benchmarking |
|
|
China - Beijing |
output-based benchmarking and grandparenting |
Upper- (120%) and lower-bounds (80%) for the share of free allowances in entities’ verified emissions for the 2022 and 2023 compliance years. |
|
China - Chongqing |
output-based benchmarking, grandparenting and “equivalence method” (free allowances are adjusted ex-post to equal verified emissions) |
|
|
China - Fujian |
output-based benchmarking and grandparenting |
For sectors using the benchmarking method allocation has upper and lower bound (resp. 120% and 80% of verified emissions). For sectors using historical intensity methods, the surplus or shortfall is limited to 3 to 10% of verified emissions. |
|
China - Guangdong |
output-based benchmarking and grandparenting |
The quota for 2023 was distributed partially free of charge and partially for a fee. |
|
China - Hubei |
output-based benchmarking and grandparenting |
|
|
China - Shanghai |
output-based benchmarking and grandparenting |
|
|
China - Shenzhen |
output-based benchmarking and grandparenting |
|
|
China - Tianjin |
output-based benchmarking and grandparenting |
|
|
China national ETS |
output-based benchmarking |
|
|
EU ETS |
benchmarking |
There are revised rules applying from Phase 4 covering adjustments to free allocation when an installation makes a significant change to its production. The threshold for adjustments is a 15% increase or decrease in production. Adjustments to free allocation are issued based on yearly activity data reports that operators submit to national competent authorities. |
|
German ETS |
n.a. |
|
|
Indonesia ETS |
output-based benchmarking |
|
|
Japan - Saitama |
grandparenting |
|
|
Japan -Tokyo |
grandparenting |
|
|
Kazakhstan ETS |
output-based benchmarking |
|
|
Korea ETS |
benchmarking and grandparenting |
|
|
Mexico ETS |
equal to verified emissions |
|
|
New Zealand ETS |
benchmarking |
|
|
Swiss ETS |
benchmarking |
Free allocation levels may be updated annually if production levels deviate at least 15 percentage points from the 2014 to 2018 base years. |
|
UK ETS |
benchmarking |
Installations eligible for free allowances must submit a verified Activity Level Report. If the data in the Activity Level Report shows an increase or decrease in activity of 15% or more from historical activity levels (calculated based on the previous two years’ activity levels), their free allocation will be recalculated. |
|
United States - California |
output-based benchmarking for industrial facilities,(1)(2) grandparenting for natural gas facilities, forecast methodology for electrical distribution utilities (fixed amount of the cap is distributed to the utilities according to each utility’s demand forecast, their supply forecast, and additional information) |
Allowances receive by electricity distributors and natural gas suppliers may not be traded. Part can be used for compliance and part should be consigned to auctions, and the resulting auction proceeds used for programs to reduce GHG emissions or return the proceeds to ratepayers as non-volumetric credits. |
|
United States - Massachusetts |
n.a. |
|
|
United States - RGGI ** |
n.a. |
|
|
United States - Washington |
output-based benchmarking for industrial facilities,(1)(2) grandparenting for natural gas facilities, forecast methodology for electrical distribution utilities (fixed amount of the cap is distributed to the utilities according to each utility’s demand forecast, their supply forecast, and additional information) |
Allowances receive by electricity distributors and natural gas suppliers may not be traded. Part can be used for compliance and part should be consigned to auctions, and the resulting auction proceeds used for programs to reduce GHG emissions or return the proceeds to ratepayers as non-volumetric credits. |
Note: * Over the course of 2023, the federal OBPS was operational in Manitoba, Nunavut, Prince Edward Island and Yukon.
** RGGI (Regional Greenhouse Gas Initiative): in 2023, it operates with ten the states of Connecticut, Delaware, Maine, Maryland, Massachusetts, New Hampshire, New Jersey, New York, Rhode Island, Vermont and Virginia.
(1) Industrial allocations are adjusted if the total sum of freely allocated allowances exceeds the cap.
(2) A small number of facilities may receive free allowances based on grandparenting.
n.a.: not applicable (since no free allowances).
Source: ICAP (2025[13]) and Authors.
References
[3] Climate Watch (2025), Historical GHG Emissions, https://www.climatewatchdata.org/ghg-emissions (accessed on 2025).
[12] Flues, F. and K. van Dender (2017), “Permit allocation rules and investment incentives in emissions trading systems”, OECD Taxation Working Papers, No. 33, OECD Publishing, Paris, https://doi.org/10.1787/c3acf05e-en.
[6] GCP (2025), The Global Carbon Project, https://www.globalcarbonproject.org/ (accessed on 22 June 2025).
[1] Greenhouse Gas Protocol (2011), “Corporate Value Chain (Scope 3) Accounting and Reporting Standard”, GHG Protocol; WRI; WBCSD, https://ghgprotocol.org/sites/default/files/standards/Corporate-Value-Chain-Accounting-Reporing-Standard_041613_2.pdf.
[13] ICAP (2025), Emissions Trading Worldwide: Status Report 2025., Berlin: International Carbon Action Partnership., https://icapcarbonaction.com/system/files/document/250409_icap_sr25_final.pdf.
[2] IEA (2025), “World Energy Balances”, IEA, Paris , Licence: Terms of Use for Non-CC Material, https://www.iea.org/data-and-statistics/data-product/world-energy-balances (accessed on 22 June 2025).
[8] IEA (2025), World Energy Balances - Database documentation, https://www.iea.org/data-and-statistics/data-product/world-energy-balances#documentation.
[11] OECD (2024), Pricing Greenhouse Gas Emissions 2024 - Support Materials, https://www.oecd.org/en/publications/pricing-greenhouse-gas-emissions-2024_b44c74e6-en/support-materials.html (accessed on 2021 May 2025).
[5] OECD (2022), Pricing Greenhouse Gas Emissions: Turning Climate Targets into Climate Action, OECD Series on Carbon Pricing and Energy Taxation, OECD Publishing, Paris, https://doi.org/10.1787/e9778969-en.
[9] OECD (2019), Taxing Energy Use 2019: Using Taxes for Climate Action, OECD Publishing, Paris, https://doi.org/10.1787/058ca239-en.
[4] OECD (2016), Effective Carbon Rates: Pricing CO2 through Taxes and Emissions Trading Systems, OECD Series on Carbon Pricing and Energy Taxation, OECD Publishing, Paris, https://doi.org/10.1787/9789264260115-en.
[10] OECD (2015), Taxing Energy Use 2015: OECD and Selected Partner Economies, OECD Publishing, Paris, https://doi.org/10.1787/9789264232334-en.
[7] World Resources Institute (2024), “Climate Watch country greenhouse gas emissions data and methodology - Technical Note”, https://files.wri.org/d8/s3fs-public/2024-05/climate-watch-country-greenhouse-gas-emissions-data-methodology.pdf.