Germany

France

United Kingdom

Global

Netherlands

Natural gas - 100% mineral blend (net CV)

Austria

Australia

Belgium

Bulgaria

Brazil

Canada

Alberta, CA

British Columbia, CA

Manitoba, CA

New Brunswick, CA

Newfoundland and Labrador, CA

Nova Scotia, CA

Northwest Territories, CA

Nunavut, CA

Ontario, CA

Prince Edward Island, CA

Quebec, CA

Saskatchewan, CA

Yukon, CA

Switzerland

China

Cyprus

Czechia

Denmark

Estonia

Spain

European Union

Finland

Greece

Croatia

Hungary

Indonesia

Ireland

India

Italy

Japan

Korea, Republic of

Lithuania

Malta

Mexico

North America

Norway

Poland

Portugal

Romania

Central Asia and Pacific Asia, Oceania, Antarctica

East Europe and Iceland

Africa except Egypt and South Africa

Latin America except Brazil

Middle East, Asia and Egypt

Russian Federation (the)

Sweden

Singapore

Slovenia

Slovakia

Türkiye

Taiwan (Province of China)

United States of America (the)

South Africa

Motor gasoline

Australian Capital Territory, AU

New South Wales, AU

Northern Territory, AU

Queensland, AU

South Australia, AU

Tasmania, AU

Victoria, AU

Western Australia, AU

New Zealand

Natural gas

Natural gas (industrial subsector)

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 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 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 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 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 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 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.

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 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 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 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 2025: 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.

Emission intensity of natural gas (based on lower heating value). Reference point final energy use at 100% utilization rate. Total life cycle incl. transport + material input without disposal. The emission factor is calculated using the Net Calorific Value. Retrieved from GEMIS v5.0.

Natural gas - lower heating value (net CV)

Emission intensity of natural gas (net CV). Retrieved from the file Base Carbone v23.3 published by ADEME. For detailed guidance on the application and interpretation of these emission factors please refer to the documentation provided by the source.

Natural gas (net CV)

Property	Value
Name	Natural gas (net CV) And 4 Other Names Natural gas (net CV) Natural gas (net calorific value) Natural gas - 100% mineral blend (net CV) Natural gas - lower heating value (net CV)
Sector	Energy
Category	Fuel
Source	ADEME, BEIS, CBAM, GEMIS, Netherlands Enterprise Agency
Region	Germany (DE), France (FR), United Kingdom (GB), Global (GLOBAL), Netherlands (NL)
Unit Type	Energy Weight
Year	2025 to 2015
LCA Activity	fuel_combustion, upstream-use_phase-transport, well_to_tank

Natural gas - 100% mineral blend (net CV)

Activity summary

API Reference

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Related factors

Fuel Emission Factors

Motor gasoline

Natural gas

Natural gas (industrial subsector)

Emission Factor Name	Region	Source	Year	Unit
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2019	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2019	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2020	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2020	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2021	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2021	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2022	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2022	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2023	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2023	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2024	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2024	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2025	Energy
Natural gas - 100% mineral blend (net CV)	United Kingdom	BEIS	2025	Energy
Natural gas - lower heating value (net CV)	Germany	GEMIS	2015	Energy
Natural gas (net CV)	France	ADEME	2024	Energy
Natural gas (net CV)	France	ADEME	2024	Energy
Natural gas (net CV)	France	ADEME	2024	Energy
Natural gas (net CV)	France	ADEME	2024	Energy
Natural gas (net CV)	France	ADEME	2024	Energy