United Kingdom

New Zealand

Petrol (100% mineral petrol)

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

Germany

Denmark

Estonia

Spain

European Union

Finland

France

Global

Greece

Croatia

Hungary

Indonesia

Ireland

India

Italy

Japan

Korea, Republic of

Lithuania

Malta

Mexico

North America

Netherlands

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-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.

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.

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.

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 2022: flat file published by the UK BEIS/Defra at the source URL.

Emission intensity of supply chain in dollars spend on: petrol. Provided by the Market Economics Limited 2023 in the Consumption Emissions Modelling report prepared for Auckland Council. Retrieved from the sheet: Cons EF 199 SUT in the excel file: consumption-emissions-modelling-market-economics-march-2023-dataset.

Petrol

Emission intensity of supply chain in GBP spend on: petrol. In actual prices in £s and including VAT. Provided by BEIS/DEFRA in the official report on GHG Emissions of the UK between 1996-2018. Where source emission factors are identical across a variety of activities they have been grouped to avoid confusion - details are documented in the OEFDB data guidance. NOTE: This dataset has been deprecated by the source and will be replaced soon.

Property	Value
Name	Petrol And 2 Other Names Petrol Petrol (100% mineral petrol)
Sector	Energy
Category	Fuel
Source	BEIS, Market Economics Limited
Region	United Kingdom (GB), New Zealand (NZ)
Unit Type	Money Volume Weight
Year	2023 to 2018
LCA Activity	fuel_combustion, unknown, well_to_tank

Petrol (100% mineral petrol)

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
Petrol (100% mineral petrol)	United Kingdom	BEIS	2022	Volume
Petrol (100% mineral petrol)	United Kingdom	BEIS	2021	Weight
Petrol (100% mineral petrol)	United Kingdom	BEIS	2023	Weight
Petrol (100% mineral petrol)	United Kingdom	BEIS	2021	Volume
Petrol (100% mineral petrol)	United Kingdom	BEIS	2023	Volume
Petrol (100% mineral petrol)	United Kingdom	BEIS	2022	Weight
Petrol (100% mineral petrol)	United Kingdom	BEIS	2023	Weight
Petrol (100% mineral petrol)	United Kingdom	BEIS	2021	Volume
Petrol (100% mineral petrol)	United Kingdom	BEIS	2022	Volume
Petrol	New Zealand	Market Economics Limited	2019	Money
Petrol (100% mineral petrol)	United Kingdom	BEIS	2023	Volume
Petrol (100% mineral petrol)	United Kingdom	BEIS	2021	Weight
Petrol	United Kingdom	BEIS	2018	Money
Petrol (100% mineral petrol)	United Kingdom	BEIS	2022	Weight