United Kingdom

Global

Italy

Netherlands

Türkiye

Liquefied petroleum gas LPG (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

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 liquefied petroleum gases. 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 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 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 2018: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of liquefied petroleum gases 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.

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 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 2020: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of liquefied petroleum gas lpg. 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.

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 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 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.

Liquefied petroleum gases (LPG) (net 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 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 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 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 2023: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of fuel combustion based on 2006 IPCC default. 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 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 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.

Property	Value
Name	Liquefied petroleum gas LPG (net CV) And 2 Other Names Liquefied petroleum gas LPG (net CV) Liquefied petroleum gases (LPG) (net CV)
Sector	Energy
Category	Fuel
Source	BEIS, CBAM, ISPRA, Netherlands Enterprise Agency, UNFCCC / Turkish Statistical Institute
Region	United Kingdom (GB), Global (GLOBAL), Italy (IT), Netherlands (NL), Türkiye (TR)
Year	2025 to 2006
LCA Activity	fuel_combustion, well_to_tank

Liquefied petroleum gas LPG (net CV)

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Natural gas distribution

Petroleum refineries

Other petroleum and coal products manufacturing

Emission Factor Name	Region	Source	Year	Unit
Liquefied petroleum gas LPG (net CV)	Global	CBAM	2023	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2019	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2021	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2018	Unit Type
Liquefied petroleum gas LPG (net CV)	Global	CBAM	2023	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2024	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2020	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2020	Unit Type
Liquefied petroleum gas LPG (net CV)	Netherlands	Netherlands Enterprise Agency	2024	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2023	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2025	Unit Type
Liquefied petroleum gases (LPG) (net CV)	Türkiye	UNFCCC / Turkish Statistical Institute	2023	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2022	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2018	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2022	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2023	Unit Type
Liquefied petroleum gas LPG (net CV)	Italy	ISPRA	2006	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2021	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2024	Unit Type
Liquefied petroleum gas LPG (net CV)	United Kingdom	BEIS	2025	Unit Type

Liquefied petroleum gas LPG (net CV)

Activity summary

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Related factors

Fuel Emission Factors

Natural gas distribution

Petroleum refineries

Other petroleum and coal products manufacturing

Detailed Metadata

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