France

United Kingdom

Global

Italy

Netherlands

Türkiye

Petroleum coke (net CV)

United Arab Emirates (the)

Afghanistan

Antigua and Barbuda

Albania

Angola

Argentina

Austria

Australia

Barbados

Bangladesh

Belgium

Burkina Faso

Bulgaria

Bahrain

Burundi

Benin

Bolivia, Plurinational State of

Brazil

Bahamas

Bhutan

Belize

Canada

Central African Republic

Congo

Switzerland

Côte d'Ivoire

Chile

Cameroon

China

Colombia

Costa Rica

Cyprus

Czechia

Germany

Denmark

Dominica

Dominican Republic

Algeria

Ecuador

Estonia

Egypt

Spain

Ethiopia

Finland

Fiji

Gabon

Grenada

Gambia

Guinea

Equatorial Guinea

Greece

Guatemala

Guinea-Bissau

Hong Kong

Honduras

Croatia

Haiti

Hungary

Indonesia

Ireland

Israel

India

Iraq

Iran, Islamic Republic of

Iceland

Jamaica

Jordan

Japan

Kenya

Cambodia

Kiribati

Saint Kitts and Nevis

Korea, Republic of

Kuwait

Kazakhstan

Lao People's Democratic Republic

Lebanon

Saint Lucia

Sri Lanka

Lesotho

Lithuania

Luxembourg

Latvia

Morocco

Moldova, Republic of

North Macedonia

Mali

Myanmar

Mongolia

Malta

Mauritius

Maldives

Malawi

Mexico

Malaysia

Namibia

Niger

Natural gas distribution

Petroleum refineries

Other petroleum and coal products manufacturing

Emission intensity of petroleum coke (net CV). Retrieved from the file Base Carbone v23.9 published by ADEME. For detailed guidance on the application and interpretation of these emission factors please refer to the documentation provided by the source.

Well-to-Tank (WTT) emission intensity of fuel. WTT fuels conversion factors should be used to account for the upstream Scope 3 emissions associated with extraction and refining and transportation of the raw fuel sources to an organisation site (or asset) - prior to combustion. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2025: flat file published by the UK BEIS/Defra at the source URL.

Well-to-Tank (WTT) emission intensity of fuel. WTT fuels conversion factors should be used to account for the upstream Scope 3 emissions associated with extraction and refining and transportation of the raw fuel sources to an organisation site (or asset) - prior to combustion. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2020: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of stationary combustion of fuel. Fuels conversion factors should be used for primary fuel sources combusted at a site or in an asset owned or controlled by the reporting organisation. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2022: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of combustion of fuel - CO2 only. Retrieved from sheet: 'Table1.A(b)' of the 2023 Excel file within the Common Reporting Tables 2025 published by UNFCCC and provided by the Turkish Statistical Institute at the source URL. The source reports a carbon emission factor in t C/TJ. To convert it to a CO2 emission factor we multiplied by 44/12.

Emission intensity of fuel combustion based on net calorific value. Published by ISPRA (Istituto Superiore per la Protezione e la Ricerca Ambientale). Retrieved from Sheet 8 of the Excel file provided by the source. Data quality flag: Partial factor - this EF includes only CO2 values; it does not include values for CH4/N2O and other greenhouse gases.

Emission intensity of stationary combustion of fuel. Fuels conversion factors should be used for primary fuel sources combusted at a site or in an asset owned or controlled by the reporting organisation. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2019: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of stationary combustion of fuel. Fuels conversion factors should be used for primary fuel sources combusted at a site or in an asset owned or controlled by the reporting organisation. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2026: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of stationary combustion of fuel. Fuels conversion factors should be used for primary fuel sources combusted at a site or in an asset owned or controlled by the reporting organisation. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2023: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of petroleum coke. Provided by the Official Journal of the European Union for the purposes of the carbon border adjustment mechanism during the transitional period. Retrieved from Annex VIII and calculated by multiplying the columns: Emission factor (t CO2/TJ) and Net calorific value (TJ/Gg) from Table 1 at the source URL. NOTE: this value is provided in CO2 only and does not include the impact of other GHGs.

Well-to-Tank (WTT) emission intensity of fuel. WTT fuels conversion factors should be used to account for the upstream Scope 3 emissions associated with extraction and refining and transportation of the raw fuel sources to an organisation site (or asset) - prior to combustion. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2022: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of stationary combustion of fuel. Fuels conversion factors should be used for primary fuel sources combusted at a site or in an asset owned or controlled by the reporting organisation. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2024: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of petroleum coke. Published by the Netherlands Enterprise Agency. Retrieved from Table 1 of the pdf file Netherlands: list of fuels and standard CO2 emission factors version of January 2024. NOTE: this value is provided in CO2 only and does not include the impact of other GHGs.

Well-to-Tank (WTT) emission intensity of fuel. WTT fuels conversion factors should be used to account for the upstream Scope 3 emissions associated with extraction and refining and transportation of the raw fuel sources to an organisation site (or asset) - prior to combustion. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2026: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of stationary combustion of fuel. Fuels conversion factors should be used for primary fuel sources combusted at a site or in an asset owned or controlled by the reporting organisation. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2020: flat file published by the UK BEIS/Defra at the source URL.

Well-to-Tank (WTT) emission intensity of fuel. WTT fuels conversion factors should be used to account for the upstream Scope 3 emissions associated with extraction and refining and transportation of the raw fuel sources to an organisation site (or asset) - prior to combustion. The emission factor is calculated using the Net Calorific Value. Retrieved from the Conversion Factors 2021: flat file published by the UK BEIS/Defra at the source URL.

Property	Value
Name	Petroleum coke (net CV)
Sector	Energy
Category	Fuel
Source	ADEME, BEIS, CBAM, ISPRA, Netherlands Enterprise Agency, UNFCCC / Turkish Statistical Institute
Region	France (FR), United Kingdom (GB), Global (GLOBAL), Italy (IT), Netherlands (NL), Türkiye (TR)
Year	2026 to 2014
LCA Activity	fuel_combustion, upstream, well_to_tank

Petroleum coke (net CV)

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Natural gas distribution

Petroleum refineries

Other petroleum and coal products manufacturing

Emission Factor Name	Region	Source	Year	Unit
Petroleum coke (net CV)	France	ADEME	2015	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2025	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2020	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2022	Unit Type
Petroleum coke (net CV)	Türkiye	UNFCCC / Turkish Statistical Institute	2023	Unit Type
Petroleum coke (net CV)	Italy	ISPRA	2023	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2019	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2026	Unit Type
Petroleum coke (net CV)	Italy	ISPRA	2022	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2023	Unit Type
Petroleum coke (net CV)	Global	CBAM	2023	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2022	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2024	Unit Type
Petroleum coke (net CV)	Netherlands	Netherlands Enterprise Agency	2024	Unit Type
Petroleum coke (net CV)	France	ADEME	2014	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2026	Unit Type
Petroleum coke (net CV)	France	ADEME	2014	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2020	Unit Type
Petroleum coke (net CV)	United Kingdom	BEIS	2021	Unit Type
Petroleum coke (net CV)	France	ADEME	2014	Unit Type

Petroleum coke (net CV)

Activity summary

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Related factors

Fuel Emission Factors

Natural gas distribution

Petroleum refineries

Other petroleum and coal products manufacturing

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