China

Germany

European Union

United Kingdom

Global

North America

Netherlands

Liquefied petroleum gas LPG

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

Cyprus

Czechia

Denmark

Estonia

Spain

Finland

France

Greece

Croatia

Hungary

Indonesia

Ireland

India

Italy

Japan

Korea, Republic of

Lithuania

Malta

Mexico

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

United Arab Emirates (the)

Afghanistan

Antigua and Barbuda

Albania

Angola

Argentina

Barbados

Bangladesh

Burkina Faso

Bahrain

Burundi

Benin

Bolivia, Plurinational State of

Bahamas

Bhutan

Belize

Central African Republic

Congo

Côte d'Ivoire

Chile

Cameroon

Colombia

Costa Rica

Dominica

Dominican Republic

Algeria

Ecuador

Egypt

Ethiopia

Fiji

Gabon

Grenada

Gambia

Guinea

Equatorial Guinea

Guatemala

Guinea-Bissau

Hong Kong

Honduras

Haiti

Israel

Iraq

Iran, Islamic Republic of

Iceland

Jamaica

Jordan

Kenya

Cambodia

Kiribati

Saint Kitts and Nevis

Kuwait

Kazakhstan

Lao People's Democratic Republic

Lebanon

Saint Lucia

Sri Lanka

Lesotho

Luxembourg

Latvia

Morocco

Moldova, Republic of

North Macedonia

Mali

Myanmar

Mongolia

Mauritius

Maldives

Malawi

Malaysia

Namibia

Niger

Natural gas distribution

Petroleum refineries

Well-to-Wheel (WTW) emission intensity of fuel. Retrieved from the Global Logistics Emissions Council Framework for Logistics Emissions Accounting and Reporting. (2019).

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. 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. 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. 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. 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. Retrieved from the Conversion Factors 2018: 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 Gross Calorific Value. Retrieved from the Conversion Factors 2022: flat file published by the UK BEIS/Defra at the source URL.

Liquefied petroleum gas LPG (gross CV)

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 Gross Calorific Value. Retrieved from the Conversion Factors 2021: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of liquefied petroleum gas lpg. Retrieved from the excel file CO2 Emissiefactoren 2024 providing a Dutch standard list of CO2 emission factors. For additional information on the application and interpretation of this emission factor please refer to the link: https://co2emissiefactoren.nl/factoren/2024/29/62/brandstoffen-voertuigen-fossiele-brandstoffen-lpg/

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 Gross 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. Retrieved from the Global Logistics Emissions Council Framework for Logistics Emissions Accounting and Reporting. (2019).

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. Retrieved from the Conversion Factors 2025: flat file published by the UK BEIS/Defra at the source URL.

Tank-to-Wheel (TTW) emission intensity of fuel. Retrieved from the Global Logistics Emissions Council Framework for Logistics Emissions Accounting and Reporting. (2019).

Emission intensity of liquefied petroleum gas. The emission factor represents greenhouse emissions from fuel combustion or use. Published by the Chinese Academy of Environmental Planning. Retrieved from the China Products Carbon Footprint Factors Database (2022).

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. Retrieved from the Conversion Factors 2023: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of liquefied petroleum gas lpg. Calculated using emission factors published by the source and converting from a net to gross calorific value basis by multiplying by 0.9. Published by the Netherlands Enterprise Agency. The net calorific value is 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. Retrieved from the Conversion Factors 2021: flat file published by the UK BEIS/Defra at the source URL.

Property	Value
Name	Liquefied petroleum gas And 3 Other Names Liquefied petroleum gas Liquefied petroleum gas LPG Liquefied petroleum gas LPG (gross CV)
Sector	Energy
Category	Fuel
Source	Bafa, BEIS, CAEP, CBAM, CO2 Emissiefactoren, GLEC, Netherlands Enterprise Agency
Region	China (CN), Germany (DE), European Union (EU), United Kingdom (GB), Global (GLOBAL), North America (N_AMERICA), Netherlands (NL)
Unit Type	Energy Volume Weight
Year	2025 to 2018
LCA Activity	fuel_combustion, fuel_upstream-fuel_combustion, tank_to_wheel, well_to_tank, well_to_wheel

Liquefied petroleum gas LPG

Activity summary

API Reference

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Related factors

Fuel Emission Factors

Motor gasoline

Natural gas distribution

Petroleum refineries

Emission Factor Name	Region	Source	Year	Unit
Liquefied petroleum gas LPG	European Union	GLEC	2019	Weight
Liquefied petroleum gas LPG	United Kingdom	BEIS	2022	Weight
Liquefied petroleum gas LPG	United Kingdom	BEIS	2021	Weight
Liquefied petroleum gas LPG	United Kingdom	BEIS	2023	Weight
Liquefied petroleum gas LPG	United Kingdom	BEIS	2025	Volume
Liquefied petroleum gas LPG	United Kingdom	BEIS	2018	Weight
Liquefied petroleum gas LPG (gross CV)	United Kingdom	BEIS	2022	Energy
Liquefied petroleum gas LPG (gross CV)	United Kingdom	BEIS	2021	Energy
Liquefied petroleum gas LPG	United Kingdom	BEIS	2023	Volume
Liquefied petroleum gas LPG	Netherlands	CO2 Emissiefactoren	2024	Volume
Liquefied petroleum gas LPG (gross CV)	United Kingdom	BEIS	2019	Energy
Liquefied petroleum gas LPG	North America	GLEC	2019	Volume
Liquefied petroleum gas LPG	European Union	GLEC	2019	Volume
Liquefied petroleum gas LPG	United Kingdom	BEIS	2025	Volume
Liquefied petroleum gas LPG	European Union	GLEC	2019	Volume
Liquefied petroleum gas LPG	China	CAEP	2022	Weight
Liquefied petroleum gas LPG	North America	GLEC	2019	Weight
Liquefied petroleum gas LPG	United Kingdom	BEIS	2023	Volume
Liquefied petroleum gas LPG (gross CV)	Netherlands	Netherlands Enterprise Agency	2024	Energy
Liquefied petroleum gas LPG	United Kingdom	BEIS	2021	Weight