Emission factors and reference values
Version 3.0
October 2025
    
    
    
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Document revision history
| Version number | Publication date | Summary of changes | 
|---|---|---|
| 3.0 | October 24, 2025 | Addition of emission factors and other reference values applicable to the Reducing Enteric Methane Emissions from Beef Cattle federal offset protocol Update of emission factors and other reference values in alignment with the National Inventory Report 1990–2023: Greenhouse Gas Sources and Sinks in Canada  | 
| 2.0 | May 6, 2024 | Addition of reference values applicable to the Improved Forest Management on Private Land federal offset protocol Update of emission factors and other reference values in alignment with the National Inventory Report 1990 – 2022: Greenhouse Gas Sources and Sinks in Canada Addition of rules on the timing applicability of emission factors and other reference values Changes to clarify the structure and facilitate the use of the document  | 
| 1.1 | June 13, 2023 | Update of information and emission factors in alignment with the April 2023 publication of the National Inventory Report 1990 – 2021: Greenhouse Gas Sources and Sinks in Canada | 
| 1.0 | June 8, 2022 | Initial version | 
1.0 Introduction
Canada's Greenhouse Gas (GHG) Offset Credit System is established under Part 2 of the Greenhouse Gas Pollution Pricing Act to provide an incentive to implement projects that result in domestic GHG reductions that would not have been generated in the absence of the project, that go beyond legal requirements and that are not subject to carbon pollution pricing mechanisms.
Canada's GHG Offset Credit System consists of:
- the Canadian Greenhouse Gas Offset Credit System Regulations (the Regulations), which establish the system, implement the operational aspects and set the general requirements applicable to all project types
 - federal offset protocols, included in the Compendium of Federal Offset Protocols (the Compendium), each containing requirements for project implementation and methods for quantifying GHG reductions for a given project type, and
 - the Credit and Tracking System (CATS) to register offset projects, issue and track offset credits, and share key information through Canada's GHG Offset Credit System Public Registry
 
The Regulations apply to a proponent of a project which is of a type for which a protocol has been included in the Compendium; that aims to generate GHG reductions by preventing GHG emissions or removing GHGs from the atmosphere; and with respect to which the GHG reductions are real, additional, quantified, verified, unique and permanent. Offset credits will be issued to a proponent of a project for the period covered by a project report in the amount determined in accordance with subsection 29(2) of the Regulations if requirements of subsection 29(1) of the Regulations are met.
As per subsection 19(1) of the Regulations, this document provides emission factors and other reference values that a proponent must use in conjunction with a federal offset protocol to quantify the GHG reductions generated by a project. It also specifies timing applicability for the emission factors and other reference values that are to be used for the quantification of GHG reductions occurring in a given calendar year.
This document is categorized into general emission factors and other reference values that are applicable to more than one federal offset protocol, and protocol-specific emission factors and other reference values. For all emission factors and other reference values, it is specified which parameter in a given protocol the emission factors or other reference values correspond to. The proponent may need to convert the units of the emission factors and other reference values provided in this document to align with the units presented in the quantification methodology of the relevant federal offset protocol.
Emission factors and other reference values are subject to periodic updates when a new federal offset protocol is included in the Compendium, or when updated versions of the sources referenced in this document are published. As per subsection 1(2) of the Regulations, proponents must use the latest version of this document.
2.0 Abbreviations and acronyms
The following abbreviations and acronyms are used in this document:
- Act: Greenhouse Gas Pollution Pricing Act
 - CH4: methane
 - CO2: carbon dioxide
 - CO2e: carbon dioxide equivalent
 - g: gram
 - kg: kilogram
 - kWh: kilowatt hour
 - L: litre
 - m3: cubic meter
 - N2O: nitrous oxide
 - SF6: sulfur hexafluoride
 - t: metric tonne
 
Emission factors and other reference values contained in this document are often sourced from the annual National inventory reports for GHG sources and sinks in Canada (NIR), published by Environment and Climate Change Canada (ECCC). To simplify references to these reports in the footnotes, a short form citation is used. The complete citation of “Environment and Climate Change Canada. (year x). National Inventory Report 1990–year y: Greenhouse Gas Sources and Sinks in Canada” is replaced by “ECCC. (year x). NIR 1990–year y.” The short form citation in the footnotes also includes the relevant part number of the report, table number and table title corresponding to the emission factor or other reference value.
3.0 General
3.1 Global warming potentials
Global warming potentials to be used for the quantification of GHG reductions are the ones published in Schedule 3 to the Act at the time GHG reductions occur.
4.0 General emission factors and other reference values
Emission factors and other reference values in Section 4.0 may be applicable to more than one federal offset protocol.
4.1 Fossil fuel combustion
Emission factors contained in Tables 1.1, and 1.2, and 1.3 correspond to the parameter EFCO2,j in applicable protocols.
Emission factors contained in Table 1.1 are to be used for the quantification of GHG reductions occurring in calendar years 2023 and 2024.
| Province / Territory | MarketableFootnote 1 * | Non-marketableFootnote 2 ** | 
|---|---|---|
| British Columbia | 1 966 | 2 162 | 
| Alberta | 1 962 | 2 109 | 
| Saskatchewan | 1 920 | 2 441 | 
| Manitoba | 1 915 | 2 401 | 
| Ontario | 1 921 | 2 401 | 
| Quebec | 1 926 | - | 
| New Brunswick | 1 919 | 2401 | 
| Nova Scotia | 1 919 | 2494 | 
| Prince Edward Island | 1 919 | - | 
| Newfoundland and Labrador | 1 919 | 2 202 | 
| Yukon | 1 966 | 2 401 | 
| Northwest Territories | 1 966 | 2 466 | 
| Nunavut | 1 966 | - | 
* The term "marketable" applies to the fuel consumed by the Utility, Industry, Residential, Commercial, and Transport subsectors.
** The term "non-marketable" applies to raw/unprocessed gas consumption, mainly by natural gas producers.
Emission factors contained in Table 1.2 are to be used for the quantification of GHG reductions occurring in calendar year 2025.
| Province / Territory | MarketableFootnote 3 | Non-marketableFootnote 4 | 
|---|---|---|
| British Columbia | 1 966 | 2 162 | 
| Alberta | 1 962 | 2 113 | 
| Saskatchewan | 1 920 | 2 441 | 
| Manitoba | 1 915 | 2 401 | 
| Ontario | 1 921 | 2 401 | 
| Quebec | 1 926 | - | 
| New Brunswick | 1 919 | 2 401 | 
| Nova Scotia | 1 919 | 2 494 | 
| Prince Edward Island | 1 919 | - | 
| Newfoundland and Labrador | 1 919 | 2 340 | 
| Yukon | 1 966 | 2 401 | 
| Northwest Territories | 1 966 | 2 466 | 
| Nunavut | 1 966 | - | 
Emission factors contained in Table 1.3 are to be used for the quantification of GHG reductions occurring in calendar year 2026.
| Province / Territory | MarketableFootnote 5 | Non-marketableFootnote 6 | 
|---|---|---|
| British Columbia | 1 966 | 2 162 | 
| Alberta | 1 962 | 2 112 | 
| Saskatchewan | 1 920 | 2 441 | 
| Manitoba | 1 915 | 2 401 | 
| Ontario | 1 921 | 2 401 | 
| Quebec | 1 926 | - | 
| New Brunswick | 1 919 | 2 401 | 
| Nova Scotia | 1 919 | 2 494 | 
| Prince Edward Island | 1 919 | - | 
| Newfoundland and Labrador | 1 919 | 2 260 | 
| Yukon | 1 966 | 2 401 | 
| Northwest Territories | 1 966 | 2 466 | 
| Nunavut | 1 966 | - | 
Emission factors contained in Tables 2.1, 2.2, and 2.3 correspond to the parameters EFCH4 or EFN2O in applicable protocols.
Emission factors contained in Table 2.1 are to be used for the quantification of GHG reductions occurring in calendar years 2023 and 2024.
| Source | CH4 | N2O | 
|---|---|---|
| Electric Utilities | 0.490 | 0.049 | 
| Industrial | 0.037 | 0.033 | 
| Producer Consumption (Non-marketable) | 6.4 | 0.060 | 
| Producer Consumption (Non-marketable) – Newfoundland and Labrador | 0.490 | 0.060 | 
| Pipelines | 1.900 | 0.050 | 
| Cement | 0.037 | 0.034 | 
| Manufacturing Industries | 0.037 | 0.033 | 
| Residential, Construction, Commercial/Institutional, Agriculture | 0.037 | 0.035 | 
Emission factors contained in Table 2.2 are to be used for the quantification of GHG reductions occurring in calendar year 2025.
| Source | CH4 | N2O | 
|---|---|---|
| Electric Utilities | 0.490 | 0.049 | 
| Industrial | 0.037 | 0.033 | 
| Producer Consumption (Non-marketable) – Newfoundland and Labrador | 0.490 | 0.060 | 
| Producer Consumption (Non-marketable) – British Columbia | 8.83Footnote 9 | 0.060 | 
Producer Consumption (Non-marketable) – Alberta  | 
8.22Footnote 9 | 0.060 | 
Producer Consumption (Non-marketable) – Saskatchewan  | 
4.64Footnote 9 | 0.060 | 
Producer Consumption (Non-marketable) – Other provinces and territories  | 
6.4 | 0.060 | 
| Pipelines | 1.900 | 0.050 | 
| Cement | 0.037 | 0.034 | 
| Manufacturing Industries | 0.037 | 0.033 | 
| Residential, Construction, Commercial/Institutional, Agriculture | 0.037 | 0.035 | 
Emission factors contained in Table 2.3 are to be used for the quantification of GHG reductions occurring in calendar year 2026.
| Source | CH4 | N2O | 
|---|---|---|
| Electric Utilities | 0.490 | 0.049 | 
| Industrial | 0.037 | 0.033 | 
| Producer Consumption (Non-marketable) – Newfoundland and Labrador | 0.490 | 0.060 | 
| Producer Consumption (Non-marketable) – British Columbia | 9.20Footnote 11 | 0.060 | 
| Producer Consumption (Non-marketable) – Alberta  | 
8.22Footnote 11 | 0.060 | 
| Producer Consumption (Non-marketable) – Saskatchewan  | 
4.20Footnote 11 | 0.060 | 
| Producer Consumption (Non-marketable) – Other provinces and territories  | 
6.4 | 0.060 | 
| Pipelines | 1.900 | 0.050 | 
| Cement | 0.037 | 0.034 | 
| Manufacturing Industries | 0.037 | 0.033 | 
| Residential, Construction, Commercial/Institutional, Agriculture | 0.037 | 0.035 | 
Emission factors contained in Tables 3.1, 3.2, and 3.3 correspond to the parameters EFCO2, EFCH4 or EFN2O in applicable protocols.
Emission factors contained in Table 3.1 are to be used for the quantification of GHG reductions occurring in calendar years 2023 and 2024.
| Fuel | CO2 | CH4 | N2O | 
|---|---|---|---|
| Propane - Residential | 1 515 | 0.027 | 0.108 | 
| Propane - All Other Uses | 1 515 | 0.024 | 0.108 | 
| Ethane | 986 | 0.024 | 0.108 | 
| Butane | 1 747 | 0.024 | 0.108 | 
Emission factors contained in Table 3.2 are to be used for the quantification of GHG reductions occurring in calendar year 2025.
| Fuel | CO2 | CH4 | N2O | 
|---|---|---|---|
| Propane - Residential | 1 515 | 0.027 | 0.108 | 
| Propane - All Other Uses | 1 515 | 0.024 | 0.108 | 
| Ethane | 986 | 0.024 | 0.108 | 
| Butane | 1 747 | 0.024 | 0.108 | 
Emission factors contained in Table 3.3 are to be used for the quantification of GHG reductions occurring in calendar year 2026.
| Fuel | CO2 | CH4 | N2O | 
|---|---|---|---|
| Propane - Residential | 1 515 | 0.027 | 0.108 | 
| Propane - All Other Uses | 1 515 | 0.024 | 0.108 | 
| Ethane | 986 | 0.024 | 0.108 | 
| Butane | 1 747 | 0.024 | 0.108 | 
Emission factors contained in Tables 4.1, 4.2, and 4.3 correspond to the parameters EFCO2, EFCH4 or EFN2O in applicable protocols.
Emission factors contained in Table 4.1 are to be used for the quantification of GHG reductions occurring in calendar years 2023 and 2024.
| Fuel | CO2 | CH4 | N2O | 
|---|---|---|---|
| Light Fuel Oil - Electric Utilities | 2 753 | 0.18 | 0.031 | 
| Light Fuel Oil - Industrial | 2 753 | 0.006 | 0.031 | 
| Light Fuel Oil - Producer Consumption | 2 670 | 0.006 | 0.031 | 
| Light Fuel Oil - Residential | 2 753 | 0.026 | 0.006 | 
| Light Fuel Oil - Forestry, Construction, Public Administration and Commercial/Institutional | 2 753 | 0.026 | 0.031 | 
| Heavy Fuel Oil - Electric Utilities | 3 156 | 0.034 | 0.064 | 
| Heavy Fuel Oil - Industrial | 3 156 | 0.12 | 0.064 | 
| Heavy Fuel Oil - Producer Consumption | 3 190 | 0.12 | 0.064 | 
| Heavy Fuel Oil - Residential, Forestry, Construction, Public Administration and Commercial/Institutional | 3 156 | 0.057 | 0.064 | 
| Kerosene - Electric Utilities | 2 560 | 0.006 | 0.031 | 
| Kerosene - Industrial | 2 560 | 0.006 | 0.031 | 
| Kerosene - Producer Consumption | 2 560 | 0.006 | 0.031 | 
| Kerosene - Residential | 2 560 | 0.026 | 0.006 | 
| Kerosene - Forestry, Construction, Public Administration and Commercial/Institutional | 2 560 | 0.026 | 0.031 | 
| Diesel - Refineries and Others | 2 681 | 0.078 | 0.022 | 
| Diesel - Upgraders | 2 681 | 0.078 | 0.022 | 
| Petroleum Coke - Refineries and Others | 3 877Footnote 16 | 0.12 | 27.5 g/m3Footnote 17 | 
| Petroleum Coke - Upgraders | 3 494Footnote 16 | 0.12 | 24.0 g/m3Footnote 17 | 
| Still Gas - Refineries and Others | 1 755 g/m3Footnote 16 | 0.032 g/m3Footnote 18 | 0.00002 | 
| Still Gas - Upgraders | 2 140 g/m3Footnote 16 | 0.000039 | 0.00002 | 
| Motor Gasoline | 2 307 | 0.100 | 0.02 | 
Emission factors contained in Table 4.2 are to be used for the quantification of GHG reductions occurring in calendar year 2025.
| Fuel | CO2 | CH4 | N2O | 
|---|---|---|---|
| Light Fuel Oil - Electric Utilities | 2 753 | 0.18 | 0.031 | 
| Light Fuel Oil - Industrial | 2 753 | 0.006 | 0.031 | 
| Light Fuel Oil - Producer Consumption | 2 670 | 0.006 | 0.031 | 
| Light Fuel Oil - Residential | 2 753 | 0.026 | 0.006 | 
| Light Fuel Oil - Forestry, Construction, Public Administration and Commercial/Institutional | 2 753 | 0.026 | 0.031 | 
| Heavy Fuel Oil - Electric Utilities | 3 156 | 0.034 | 0.064 | 
| Heavy Fuel Oil - Industrial | 3 156 | 0.12 | 0.064 | 
| Heavy Fuel Oil - Producer Consumption | 3 190 | 0.12 | 0.064 | 
| Heavy Fuel Oil - Residential, Forestry, Construction, Public Administration and Commercial/Institutional | 3 156 | 0.057 | 0.064 | 
| Kerosene - Electric Utilities | 2 560 | 0.006 | 0.031 | 
| Kerosene - Industrial | 2 560 | 0.006 | 0.031 | 
| Kerosene - Producer Consumption | 2 560 | 0.006 | 0.031 | 
| Kerosene - Residential | 2 560 | 0.026 | 0.006 | 
| Kerosene - Forestry, Construction, Public Administration and Commercial/Institutional | 2 560 | 0.026 | 0.031 | 
| Diesel - Refineries and Others | 2 681 | 0.078 | 0.022 | 
| Diesel - Upgraders | 2 681 | 0.078 | 0.022 | 
| Petroleum Coke - Refineries and Others | 3 776Footnote 20 | 0.12 | 27.5 g/m3Footnote 21 | 
| Petroleum Coke - Upgraders | 3 494Footnote 20 | 0.12 | 24.0 g/m3Footnote 21 | 
| Still Gas - Refineries and Others | 1 780 g/m3Footnote 20 | 0.032 g/m3Footnote 22 | 0.00002 | 
| Still Gas - Upgraders | 2 140 g/m3ootnote 20 | 0.000039 | 0.00002 | 
| Motor Gasoline | 2 307 | 
0.100 | 0.02 | 
Emission factors contained in Table 4.3 are to be used for the quantification of GHG reductions occurring in calendar year 2026.
| Fuel | CO2 | CH4 | N2O | 
|---|---|---|---|
| Light Fuel Oil - Electric Utilities | 2 753 | 0.18 | 0.031 | 
| Light Fuel Oil - Industrial | 2 753 | 0.006 | 0.031 | 
| Light Fuel Oil - Producer Consumption | 2 670 | 0.006 | 0.031 | 
| Light Fuel Oil - Residential | 2 753 | 0.026 | 0.006 | 
| Light Fuel Oil - Forestry, Construction, Public Administration and Commercial/Institutional | 2 753 | 0.026 | 0.031 | 
| Heavy Fuel Oil - Electric Utilities | 3 156 | 0.034 | 0.064 | 
| Heavy Fuel Oil - Industrial | 3 156 | 0.12 | 0.064 | 
| Heavy Fuel Oil - Producer Consumption | 3 190 | 0.12 | 0.064 | 
| Heavy Fuel Oil - Residential, Forestry, Construction, Public Administration and Commercial/Institutional | 3 156 | 0.057 | 0.064 | 
| Kerosene - Electric Utilities | 2 560 | 0.006 | 0.031 | 
| Kerosene - Industrial | 2 560 | 0.006 | 0.031 | 
| Kerosene - Producer Consumption | 2 560 | 0.006 | 0.031 | 
| Kerosene - Residential | 2 560 | 0.026 | 0.006 | 
| Kerosene - Forestry, Construction, Public Administration and Commercial/Institutional | 2 560 | 0.026 | 0.031 | 
| Diesel - Refineries and Others | 2 681 | 0.078 | 0.022 | 
| Diesel - Upgraders | 2 681 | 0.078 | 0.022 | 
| Petroleum Coke - Refineries and Others | 3 254Footnote 24 | 0.12 | 23.6 g/m3Footnote 25 | 
| Petroleum Coke - Upgraders | 2 717Footnote 24 | 0.12 | 18.7 g/m3Footnote 25 | 
| Still Gas - Refineries and Others | 1 773 g/m3Footnote 24 | 0.032 g/m3Footnote 26 | 0.00002 | 
| Still Gas - Upgraders | 2 140 g/m3Footnote 24 | 0.000039 | 0.00002 | 
| Motor Gasoline | 2 307 | 0.100 | 0.02 | 
4.2 Grid electricity consumption
A ‘consumption intensity’ indicator is derived to reflect the GHG emissions intensity of electricity as it is delivered to the consumer.
Emission factorsReference values contained in Tables 5.1, 5.2, and 5.3 correspond to the parameter EFEL,GHG in applicable protocols.
Emission factorsReference values contained in Table 5.1 are to be used for the quantification of GHG reductions occurring in calendar years 2023 and 2024.
| Province / Territory | Consumption intensityFootnote 28 | 
|---|---|
| British Columbia | 15 | 
| Alberta | 540 | 
| Saskatchewan | 730 | 
| Manitoba | 2.0 | 
| Ontario | 30 | 
| Quebec | 1.7 | 
| New Brunswick | 300 | 
| Nova Scotia | 690 | 
| Prince Edward IslandFootnote 29 | 300 | 
| Newfoundland and Labrador | 17 | 
| Yukon | 80 | 
| Northwest Territories | 170 | 
| Nunavut | 840 | 
Emission factors contained in Table 5.2 are to be used for the quantification of GHG reductions occurring in calendar year 2025.
| Province / Territory | Consumption intensityFootnote 31 | 
|---|---|
| British Columbia | 15 | 
| Alberta | 490 | 
| Saskatchewan | 670 | 
| Manitoba | 1.4 | 
| Ontario | 38 | 
| Quebec | 1.7 | 
| New Brunswick | 350 | 
| Nova Scotia | 700 | 
| Prince Edward IslandFootnote 32 | 350 | 
| Newfoundland and Labrador | 18 | 
| Yukon | 70 | 
| Northwest Territories | 190 | 
| Nunavut | 820 | 
Emission factors contained in Table 5.3 are to be used for the quantification of GHG reductions occurring in calendar year 2026.
| Province / Territory | Consumption intensityFootnote 34 | 
|---|---|
| British Columbia | 18 | 
| Alberta | 438 | 
| Saskatchewan | 631 | 
| Manitoba | 2.5 | 
| Ontario | 59 | 
| Quebec | 1.9 | 
| New Brunswick | 234 | 
| Nova Scotia | 581 | 
| Prince Edward IslandFootnote 35 | 234 | 
| Newfoundland and Labrador | 17 | 
| Yukon | 74 | 
| Northwest Territories | 420 | 
| Nunavut | 800 | 
4.3 Biogas combustion
Biogas includes landfill gas.
Emission factors contained in Tables 6.1, 6.2, and 6.3 correspond to the parameter EFLFG,N2O in applicable protocols.
Emission factors contained in Table 6.1 are to be used for the quantification of GHG reductions occurring in calendar years 2023 and 2024.
| Description | N2O | 
|---|---|
| Combustion of biogas for energy through a boiler, turbine, internal combustion engine or station for natural gas network | 0.005 | 
| Flaring of biogasFootnote 37 | 0 | 
Emission factors contained in Table 6.2 are to be used for the quantification of GHG reductions occurring in calendar year 2025.
| Description | N2O | 
|---|---|
| Combustion of biogas for energy through a boiler, turbine, internal combustion engine or station for natural gas network | 0.005 | 
| Flaring of biogasFootnote 39 | 0.005 | 
Emission factors contained in Table 6.3 are to be used for the quantification of GHG reductions occurring in calendar year 2026.
| Description | N2O | 
|---|---|
| Combustion of biogas for energy through a boiler, turbine, internal combustion engine or station for natural gas network | 0.005 | 
| Flaring of biogasFootnote 39 | 0.005 | 
5.0 Protocol-specific emission factors and other reference values
Emission factors and other reference values in Section 5.0 are only applicable to the federal offset protocol specified.
5.1 Improved forest management on private land
Reference values contained in Tables 7 and 8 are to be used for the quantification of GHG reductions generated by projects implemented following the Improved Forest Management on Private Land protocol and occurring from calendar year 2024 onwards.
Reference values contained in Table 7 correspond to the parameter PCi,C in the protocol.
| Wood product class | Percentage of harvest (%) | 
|---|---|
| Softwood lumber | 37.76 | 
| Hardwood lumber | 0.38 | 
| Pulp and paper | 34.60 | 
| Panels (plywood and oriented strandboard) | 12.42 | 
| Other industrial roundwood | 3.55 | 
| Fuelwood | 11.29 | 
Reference values contained in Table 8 correspond to the parameter SFj in the protocol.
| Wood product class | 100-year storage factor | 
|---|---|
| Softwood lumber | 0.213 | 
| Hardwood lumber | 0.156 | 
| Softwood plywood | 0.215 | 
| Oriented strandboard | 0.285 | 
| Non-structural panels | 0.174 | 
| Other industrial roundwood | 0.149 | 
| Fuelwood | 0 | 
| Pulp and paper | 0 | 
5.2 Reducing enteric methane emissions from beef cattle
Emission factors and other reference values contained in Tables 9 to 12 are to be used for the quantification of GHG reductions generated by projects implemented following the Reducing Enteric Methane Emissions from Beef Cattle protocol and occurring from calendar year 2025 onwards.
Reference values contained in Table 9 correspond to the parameter Ym in the protocol.
| Diet description | Enteric CH4 conversion factor (Ym) | 
|---|---|
| Diets of more than 75% low to medium quality forage containing < 60% total digestible nutrients | 0.07 | 
| Diets of more than 75% high quality forage containing ≥ 60% total digestible nutrients | 0.063 | 
| Mixed diets with forage content of 15 to 75% and the total diet is mixed with grain | 0.063 | 
| All other grains with 0 to 15% forage | 0.04 | 
| Steam-flaked corn and ionophore supplement with 0 to 10% forage | 0.03 | 
Emission factors contained in Table 10 correspond to the parameter EFlip in the protocol.
| Supplemented lipid added (%) | Emission factor (EFlip) | 
|---|---|
| < 1.0 | 1.0 | 
| 1.0 to 1.99 | 0.96 | 
| 2.0 to 2.99 | 0.92 | 
| 3.0 to 3.99 | 0.88 | 
| 4.0 to 4.99 | 0.84 | 
| ≥ 5.0 | 0.80 | 
Emission factors and other reference values contained in Table 11 correspond to the parameters MCF, EFMS, Fracv, and FracL in the protocol.
| Manure storage systemFootnote 44 | CH4 conversion factor (MCF)Footnote 45 | Emission factor for direct N2O emissions (EFMS)Footnote 46 | Fraction of nitrogen (N) excreted in manure that volatilizes (Fracv)Footnote 47 | Fraction of N excreted in manure leached (FracL)Footnote 48 | 
|---|---|---|---|---|
| Solid storage and dry lot | 0.02 | 0.02 | 0.3 | 0.03 | 
| Liquid, slurry or pit storage below confinements | 0.2 | 0.001 | 0.4 | 0 | 
| Other manure storage system | 0.01 | 0.005 | 0.24Footnote 48 | 0.05 | 
Emission factors contained in Table 12 correspond to the parameter EFV in the protocol.
| Ecozone | Emission factor for indirect N2O emissions from volatilization of manure (EFV) | 
|---|---|
| Taiga Plains | 0.005 | 
| Boreal Shield | 0.014 | 
| Atlantic Maritime | 0.014 | 
| Mixedwood Plains | 0.014 | 
| Boreal Plains | 0.005 | 
| Prairies | 0.005 | 
| Pacific Maritime | 0.014 | 
| Montane Cordillera | 0.005 |