United Kingdom

Global

Petrol - 100% mineral petrol (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

France

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

Italy

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 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 2018: 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.

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.

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 2024: 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.

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.

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.

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 2018: 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 2021: 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 2023: 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 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 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 2022: 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 2019: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of motor gasoline related to the net calorific value (NCV). 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 - Table 1 at the source URL. NOTE: this value is provided in CO2 only and does not include the impact of other GHGs.

Motor gasoline (net CV)

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 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.

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 2026: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of motor gasoline. 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.

Property	Value
Name	Motor gasoline (net CV) And 2 Other Names Motor gasoline (net CV) Petrol - 100% mineral petrol (net CV)
Sector	Energy
Category	Fuel
Source	BEIS, CBAM
Region	United Kingdom (GB), Global (GLOBAL)
Year	2026 to 2018
LCA Activity	fuel_combustion, well_to_tank

Petrol - 100% mineral petrol (net CV)

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Fuel Emission Factors

Natural gas distribution

Petroleum refineries

Other petroleum and coal products manufacturing

Emission Factor Name	Region	Source	Year	Unit
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2018	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2020	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2019	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2024	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2020	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2021	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2026	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2018	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2021	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2023	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2025	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2022	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2022	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2019	Unit Type
Motor gasoline (net CV)	Global	CBAM	2023	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2024	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2023	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2025	Unit Type
Petrol - 100% mineral petrol (net CV)	United Kingdom	BEIS	2026	Unit Type
Motor gasoline (net CV)	Global	CBAM	2023	Unit Type

Petrol - 100% mineral petrol (net CV)

Activity summary

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Interested in licensing this data?

Related factors

Fuel Emission Factors

Natural gas distribution

Petroleum refineries

Other petroleum and coal products manufacturing

Detailed Metadata

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