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Land-based greenhouse gas emissions and removals

Greenhouse gas (GHG) emissions are the major drivers of climate change. Land use activities (such as timber harvesting and land conversion) as well as natural disturbances (such as forest fires and insect infestations) result in GHG emissions. Land use activities can also result in GHG removals. For example, as forests grow or recover, carbon is removed from the atmosphere and converted into biomass by trees. Tracking the trends in Canada's land-based GHG emissions and removals can help us understand how land management decisions could reduce emissions and increase removals over time.

The indicator provides annual estimates of Canada's GHG emissions and removals from managed lands. These are lands influenced by human intervention to perform production, ecological or social functions. Examples include agricultural land, wetlands, settlements, and managed forests.

National

National land-based greenhouse gas emissions and removals

Key results

  • In 2024,
    • Natural disturbances accounted for net emissions of about 430 megatonnes of carbon dioxide equivalent (Mt CO2 eq)
    • Human activities accounted for net emissions of 4.7 Mt CO2 eq
  • Between 1990 and 2001, estimates of land-based GHGs showed more removals than emissions in all years except for 1995 (net emissions of 150 Mt CO2 eq), 1998 (net emissions of 130 Mt CO2 eq) and 1999 (net emissions of 8.0 Mt CO2 eq)
  • Since 2002, estimates show net emissions ranging between 29 Mt CO2 eq and 1,000 Mt CO2 eq, driven mainly by wildfire emissions

National land-based greenhouse gas emissions and removals, Canada, 1990 to 2024

National land-based greenhouse gas emissions and removals, 1990 to 2024 (see data table below for the long description)
Data table for the long description
National land-based greenhouse gas emissions and removals, Canada, 1990 to 2024
Year Natural disturbances
(megatonnes of carbon dioxide equivalent)
Human activities
(megatonnes of carbon dioxide equivalent)
Net exchange
(megatonnes of carbon dioxide equivalent)
1990 -130 62 -64
1991 -91 52 -39
1992 -140 63 -77
1993 -95 75 -20
1994 -89 64 -24
1995 78 74 150
1996 -80 62 -18
1997 -120 60 -62
1998 80 52 130
1999 -47 55 8.0
2000 -100 63 -41
2001 -68 48 -20
2002 44 79 120
2003 29 76 100
2004 91 75 170
2005 8.0 82 90
2006 42 61 100
2007 53 59 110
2008 14 47 61
2009 26 15 41
2010 81 41 120
2011 100 41 140
2012 83 27 110
2013 23 29 52
2014 140 6.9 150
2015 230 42 270
2016 84 26 110
2017 200 20 220
2018 240 24 260
2019 140 17 150
2020 2.7 26 29
2021 290 15 300
2022 89 46 130
2023 1,000 -8.4 1,000
2024 430 4.7 430

Note: Data are accurate to 2 significant figures. Net exchange is calculated by subtracting removals from emissions.

Download data file (Excel/CSV; 1.83 kB)
How this indicator was calculated

Note: Natural disturbances refer to emissions and removals related to wildfires and large insect infestations of the forest. Human activities refer to emissions and removals from managed lands (such as settlements, forested lands, agricultural land and wetlands) as well as transfers to harvested wood products. For more information, see the section on emissions and removals from human activities.
Source: Environment and Climate Change Canada (2026) National Inventory Report 1990-2024: Greenhouse gas sources and sinks in Canada.

Natural disturbances, such as forest fires and large insect infestations, have occurred in Canada's forests for thousands of years. These disturbances are part of the natural life cycle of the forest and generally help the forest renew itself. However, evidence demonstrates that climate change is driving an increase in natural disturbances. These disturbances can contribute to emissions of large amounts of GHGs into the atmosphere through the burning and decaying of dead trees, as well as significant removals as the forest regenerates over time.Footnote 1

For the past 20 years, the total managed forest’s net GHG exchange (that is, the land-based GHG emissions minus removals) has been significantly impacted by these natural disturbances. In 2002, the net exchange shifted from removals to emissions as a result of an increase in emissions from natural disturbances.

In managed forests, emissions and removals due to natural disturbances are associated with human activities under specific circumstances. These circumstances are described in the methods section.

Human activities

Land-based GHG emissions and removals from human activities

Land-based GHG emissions and removals from human activities are commonly referred to as land use, land-use change and forestry (LULUCF) according to international standards.

Key results

  • In 2024,
    • Most of the categories of land use activities emitted GHGs, with the Wetlands being the largest emitter (5.4 megatonnes of carbon dioxide equivalent [Mt CO2 eq])
    • Agricultural land recorded the largest removals of GHGs (3.4 Mt CO2 eq)
  • Between 1990 and 2024, human activities on managed lands resulted in net emissions for all years (except 2023), ranging between 4.7 Mt CO2 eq and 82 Mt CO2 eq
  • Human activities accounted for net emissions of 4.7 Mt CO2 eq in 2024, which is lower than the level observed in 1990 (62 Mt CO2)

Land-based greenhouse gas emissions and removals from human activities by activity sector, Canada, 1990 to 2024

 Land-based greenhouse gas emissions and removals from human activities by activity sector, Canada, 1990 to 2024 (see data table below for the long description)
Data table for the long description
Land-based greenhouse gas emissions and removals from human activities by activity sector, Canada, 1990 to 2024
Year Forest sector
(megatonnes of carbon dioxide equivalent)
Agricultural land
(megatonnes of carbon dioxide equivalent)
Wetlands
(megatonnes of carbon dioxide equivalent)
Settlements
(megatonnes of carbon dioxide equivalent)
Net exchange
(megatonnes of carbon dioxide equivalent)
1990 41 5.9 10 5.0 62
1991 39 -1.6 9.8 5.1 52
1992 48 1.0 9.5 4.8 63
1993 53 8.4 9.0 4.4 75
1994 56 -4.6 8.6 4.2 64
1995 67 -6.3 8.8 3.8 74
1996 54 -5.0 8.4 4.5 62
1997 56 -8.5 8.2 4.2 60
1998 43 -4.4 8.2 4.4 52
1999 56 -14 8.3 4.4 55
2000 67 -16 7.5 4.4 63
2001 45 -9.4 7.3 4.6 48
2002 60 6.9 7.3 5.0 79
2003 54 9.8 7.3 4.9 76
2004 85 -22 7.2 5.3 75
2005 89 -20 7.0 5.2 82
2006 72 -24 6.8 5.7 61
2007 63 -17 6.9 5.6 59
2008 53 -19 6.9 5.9 47
2009 37 -34 6.8 4.8 15
2010 50 -20 6.6 4.9 41
2011 43 -13 6.2 5.2 41
2012 36 -21 6.2 5.7 27
2013 38 -22 6.4 6.3 29
2014 34 -40 6.3 6.4 6.9
2015 37 -7.7 6.0 6.4 42
2016 27 -13 6.1 6.4 26
2017 27 -19 5.8 5.5 20
2018 33 -19 5.6 5.0 24
2019 18 -12 5.6 5.0 17
2020 26 -10 5.6 4.8 26
2021 18 -14 6.0 4.7 15
2022 12 24 5.7 4.6 46
2023 2.1 -21 5.6 4.7 -8.4
2024 -1.7 -3.4 5.4 4.4 4.7

Note: Data are accurate to 2 significant figures. Net exchange is calculated by subtracting removals from emissions.

Download data file (Excel/CSV; 2.22 kB)
How this indicator was calculated

Note: Greenhouse gas exchange from the forest sector considers emissions and removals from managed forests and transfers to and from the harvested wood products pool. Harvested wood products originate from forest trees with contributions of bioenergy from urban trees and agricultural land. As such, the reported forest sector emissions may differ at times from some information presented in the National Inventory Report For more information, see Chapter 6.4 of the National Inventory Report.
Source: Environment and Climate Change Canada (2026) National Inventory Report 1990-2024: Greenhouse Gas Sources and Sinks in Canada.

Forest sector

The forest sector category refers to emissions and removals from forest management activities such as timber harvesting, thinning and replanting and ecological processes, such as tree growth and decomposition. It also includes transfers to and disposals from the harvested wood products pool, which are the wood materials removed from the harvested site and turned into consumer products, such as timber for construction, furniture or paper products. The carbon removed from the atmosphere by trees is stored in the harvested wood products and eventually emitted back into the atmosphere or transferred into the waste stream where the product is disposed.

In 2024, the human-driven GHG flux from the forest sector was a net removal of 1.7 Mt CO2 eq. While overall forest growth on managed lands typically removes carbon from the atmosphere, disturbances – including harvest and decomposition – can result in net emissions from forests. For example, in 2024, natural ongoing ecological processes in Canadian forests resulted in net removals of 1.2 Mt CO2 eq. At the same time, 0.63 Mt CO2 eq. of carbon was stored in harvested wood products. Refer to Table 6-1 of the National Inventory Report for more information (ECCC 2026).

GHG flux from the forest sector varied between 1990 and 2024, peaking at 89 Mt CO2 eq in 2005 and since, decreasing to a removal of 1.7 Mt CO2 eq in 2024. These variations are related to harvest rates over the past several decades, particularly in the Mountain and Boreal regions, and had also increased indirectly due to a rise in natural disturbances. Natural disturbances indirectly impact GHG emissions in the forest sector through the decomposition of trees killed by low-level insect disturbances and through the reduction of managed land area where commercially growing trees remove carbon.

As forest harvest expanded in Canada, in the decades prior to 2005, increasing areas were converted to emissions sources. When forests are harvested, the sites act as emission sources over many years following the disturbance because of the decaying debris left on the site and the slow regrowth of woody biomass. Furthermore, large proportions of harvested wood were used for short-lived products (such as paper) where the carbon is rapidly transferred out of the harvested wood product pool to the waste stream or used for bioenergy. These emissions were not fully offset by the removals from the regrowth of the historically harvested areas.

Since 2004, the rate of area harvested in Canada has leveled off, and in recent years removals from the land that was historically harvested are increasing at a greater rate than the emissions resulting from new harvests. Forest carbon emissions peaked in 2005 and have since decreased. This decreasing trend in emissions happened as carbon stocks in solid wood products have continued to increase, while those in paper products have declined since 2005. Additionally, since the early 2000s, most wood waste has been used for bioenergy production (converting biomass to energy), reducing transfers of wood to solid waste disposal where it is a source of methane.

The forest industry and carbon
The forest industry and carbon

Canada's forest industry is important and understanding how tree harvesting impacts emissions and removals of carbon dioxide (CO2) to and from the atmosphere supports better decision making. Harvesting is part of a larger set of forest management activities, such as forest inventory and planning, planting, thinning, fire control, and pest management, which are carried out by provinces and territories applying sustainable practices. Because these activities are connected and part of the forest planning process, the effects of harvesting can't be measured on their own. Instead, changes in forest carbon in the managed forests are tracked as a whole, in accordance with international guidelines.

When trees are harvested, the existing dead material on the ground and new harvest residues break down, releasing CO₂. As trees grow back, the new tree growth removes little carbon at first, but removals increase over time. After a period of time, CO₂ removals resulting from tree growth equal and become greater than the emissions from the decomposing material and harvested sites become carbon sinks again.

The trees that are harvested contain carbon that becomes forest products such as building lumber and paper, but also produce wood waste. Carbon stored in wood products can stay locked away for decades, adding to a global supply of stored carbon. Waste wood is burned for energy in homes and industries, releasing the carbon stored in wood as an emission. Wood products and bioenergy also help reduce fossil emissions by replacing more carbon intensive materials like coal, oil, concrete and steel.

The carbon in forests is cycled between the trees, the wood products, the soil and the atmosphere. While the harvested forest regrows, it absorbs and stores carbon. When wood products reach the end of their use, whether short- or long-lasting, their carbon is reported as an emission.Footnote 2 Wood waste in landfills produces methane, a powerful GHG, but these emissions are counted in the Waste sector of the country where the wood products are buried. Since trees take in carbon from the air through photosynthesis, releasing it later doesn't add new CO₂ like burning fossil fuels does.

Like many industries, forest harvesting and the transformation of harvested trees into forest products involves a wide range of activities that result in fossil fuel emissions that are reported in different parts of Canada's National Inventory Report (NIR): Energy, Industry, and Waste. Where possible, the emissions from these activities are reported separately in Table 2–12 of the National GHG Inventory Report along with all emissions and changes in carbon associated with harvest. Fuel used by machines during tree harvesting is counted in the Energy-Transport sector. However, fuel used to transport the harvested wood away from the site isn't reported because the fuel used specifically by transport trucks for wood transport cannot be isolated in national fuel-use data.

Agricultural land

The agricultural land category reports emissions and removals from annual and perennial cropland, as well as from forest lands and grassland converted to cropland. Cropland includes lands in annual crops, summerfallowFootnote 3 and perennial crops. Managed agricultural grassland refers to rangeland that is used only for grazing domestic livestock.

Since 1990, agricultural land has typically contributed to GHG removals and consistently did so between 2004 and 2021. Removals by agricultural land has ranged between 1.6 Mt CO2 eq to 40 Mt CO2 eq. These removals are due to changes in agricultural practices, such as the adoption of conservation tillage,Footnote 4 increases in crop yield, and the reduced use of summerfallow. However, the removal rate from agricultural land has been decreasing in recent years due to a decline in the adoption rate of conservation tillage and the area of land used to grow perennial crops as well as increases in the conversion of forested land to agricultural land. The shift from net removals to emissions in 2022 was primarily driven by a significant drought in 2021, which reduced crop yields and carbon inputs from residues resulting in a very small loss of soil carbon over large areas of the Prairies. In 2023, crop yields were more consistent with recent harvests and soils returned to a net carbon sink again.

Wetlands

The wetlands category includes activities such as peat extraction for use in horticulture, peatland disturbances due to resource extraction activities, and flooding of land for reservoir development.

Trends in wetlands are mainly driven by the creation of large hydroelectric reservoirs occurring before 1990, resulting in higher emissions in the early 1990s. Emissions from reservoirs declined from 1990 to 2024 as emissions from submerged biomass and soils decreased over time. Emissions from drained and excavated wetlands for peat extraction increased, while emissions from disturbances related to resource extraction have remained relatively small but have increased slightly over time. Overall, during this period, total emissions declined from 10 Mt CO2 eq to 5.4 Mt CO2 eq.

Settlements

The settlements category refers to emissions and removals occurring on developed lands (such as urban environments, transport infrastructure, oil and gas infrastructure and mining) and from the conversion of land to settlements.

Total emissions for settlements fluctuated between 3.8 Mt CO2 eq and 6.4 Mt CO2 eq over the time series. Emissions were mainly driven by rates of forested land converted to settlements, with smaller contributions from wetlands linked to resource extraction activities and native grassland in northern Canada (tundra), both associated with urban and industrial expansion. These emissions are partially offset by the storage of carbon in urban trees, which provide average annual removals of about 4.0 Mt CO2 eq. Refer to Section 6.8 of the National Inventory Report for more information.

Regional

Regional land-based GHG emissions and removals from human activities

Key results

  • From 1990 to 2024,
    • The West coast region consistently emitted GHGs, but showed a decrease in emissions from 22 megatonnes of carbon dioxide equivalent (Mt CO2 eq) to 5.1 Mt CO2 eq
    • The Mountain region, which is important for forestry, shifted from removals to emissions. It had been the region contributing the most to removals in 1990 (26 Mt CO2 eq) but switched to emissions in 2002 onward, with emissions peaking in 2011 (36 Mt CO2 eq)
    • The Boreal region showed fluctuations in the net exchanges, switching from removals prior to 1993, to emissions until 2008, then back to removals after that
    • The Prairies region consistently showed removals from 1990 to 2021 (ranging between 0.5 Mt CO2 eq and 39 Mt CO2 eq) and experienced emissions for the first time in 2022 (12 Mt CO2 eq) as a result of the 2021 drought
    • The Southeastern region shifted from emissions of 24 Mt CO2 eq to removals of 4.2 Mt CO2 eq

Regional land-based greenhouse gas emissions and removals from human activities, Canada, 1990 to 2024

 Regional land-based emissions and removals from human activities, Canada, 1990 to 2024 (see data table below for the long description)
Data table for the long description
Regional land-based greenhouse gas emissions and removals from human activities, Canada, 1990 to 2024
Region Year Forest sector
(megatonnes of carbon dioxide equivalent)
Agricultural land
(megatonnes of carbon dioxide equivalent)
Wetlands
(megatonnes of carbon dioxide equivalent)
Settlements
(megatonnes of carbon dioxide equivalent)
Net exchange
(megatonnes of carbon dioxide equivalent)
Mountain 1990 -29 0.98 0.62 1.6 -26
Mountain 1991 -19 0.81 0.59 1.9 -16
Mountain 1992 -14 0.88 0.56 1.4 -11
Mountain 1993 -11 0.60 0.54 1.3 -8.8
Mountain 1994 -12 0.61 0.51 1.4 -9.4
Mountain 1995 -10 0.62 0.49 1.3 -8.0
Mountain 1996 -10 0.47 0.48 1.1 -7.7
Mountain 1997 -10 0.49 0.46 1.2 -8.3
Mountain 1998 -13 0.50 0.44 1.1 -11
Mountain 1999 -7.9 0.34 0.43 1.2 -5.9
Mountain 2000 -3.8 0.40 0.42 1.2 -1.8
Mountain 2001 -6.4 0.45 0.40 1.1 -4.5
Mountain 2002 2.3 0.40 0.39 1.0 4.1
Mountain 2003 4.3 0.51 0.38 1.0 6.2
Mountain 2004 19 0.35 0.37 1.1 21
Mountain 2005 28 0.29 0.36 1.0 30
Mountain 2006 30 0.33 0.35 1.1 32
Mountain 2007 32 0.30 0.34 1.1 34
Mountain 2008 31 0.30 0.33 1.0 33
Mountain 2009 29 0.29 0.32 0.85 30
Mountain 2010 33 0.30 0.31 0.90 35
Mountain 2011 34 0.34 0.30 1.2 36
Mountain 2012 31 0.34 0.30 1.2 33
Mountain 2013 32 0.25 0.29 1.2 34
Mountain 2014 29 0.22 0.28 1.0 31
Mountain 2015 28 0.28 0.27 0.94 30
Mountain 2016 26 0.41 0.27 0.94 28
Mountain 2017 27 0.47 0.26 0.92 29
Mountain 2018 30 0.30 0.25 0.79 31
Mountain 2019 24 0.43 0.25 0.80 25
Mountain 2020 22 0.42 0.24 0.73 24
Mountain 2021 21 0.45 0.24 0.74 23
Mountain 2022 18 0.41 0.23 0.73 19
Mountain 2023 13 0.35 0.22 0.72 14
Mountain 2024 10 0.45 0.22 0.70 11
Boreal 1990 -27 8.5 8.7 4.1 -5.7
Boreal 1991 -30 7.0 8.3 4.1 -10
Boreal 1992 -21 6.1 8.0 4.2 -3.1
Boreal 1993 -16 8.0 7.5 4.1 3.7
Boreal 1994 -7.2 3.1 7.2 4.0 7.1
Boreal 1995 5.2 1.4 7.4 4.0 18
Boreal 1996 -3.7 2.2 7.0 4.4 10
Boreal 1997 2.5 3.5 6.8 4.2 17
Boreal 1998 -1.6 2.4 6.8 4.4 12
Boreal 1999 6.0 0.97 6.9 4.4 18
Boreal 2000 14 0.43 6.1 4.5 25
Boreal 2001 3.6 0.81 5.9 4.8 15
Boreal 2002 11 3.7 5.9 5.3 26
Boreal 2003 8.0 6.8 5.9 5.2 26
Boreal 2004 17 -1.9 5.8 5.5 26
Boreal 2005 16 0.87 5.6 5.7 28
Boreal 2006 1.7 -1.9 5.4 6.2 11
Boreal 2007 -4.9 0.17 5.6 6.1 7.0
Boreal 2008 -11 -0.56 5.5 6.5 -0.08
Boreal 2009 -20 -1.7 5.4 5.7 -10
Boreal 2010 -11 0.19 5.2 5.7 -0.27
Boreal 2011 -18 2.0 4.9 5.7 -5.6
Boreal 2012 -20 -2.3 4.9 5.8 -11
Boreal 2013 -20 1.1 5.0 6.3 -7.3
Boreal 2014 -20 -4.1 5.0 6.7 -13
Boreal 2015 -17 2.4 4.7 6.4 -3.2
Boreal 2016 -23 0.40 4.8 6.4 -11
Boreal 2017 -22 0.96 4.5 5.7 -11
Boreal 2018 -21 -1.6 4.3 5.5 -12
Boreal 2019 -23 1.8 4.3 5.5 -12
Boreal 2020 -14 3.4 4.2 5.6 -0.53
Boreal 2021 -19 5.5 4.7 5.4 -3.0
Boreal 2022 -20 8.4 4.3 5.4 -1.5
Boreal 2023 -20 0.52 4.2 5.3 -10
Boreal 2024 -19 4.7 4.1 5.2 -5.2
West coast 1990 22 0.24 0.12 -0.08 22
West coast 1991 23 0.22 0.11 -0.24 23
West coast 1992 25 0.23 0.11 -0.21 25
West coast 1993 25 0.13 0.11 -0.28 25
West coast 1994 24 0.21 0.11 -0.42 24
West coast 1995 24 0.14 0.11 -0.64 23
West coast 1996 22 0.17 0.11 -0.24 22
West coast 1997 21 0.18 0.10 -0.39 21
West coast 1998 18 0.19 0.10 -0.45 18
West coast 1999 20 0.11 0.10 -0.69 20
West coast 2000 20 0.16 0.10 -0.68 20
West coast 2001 17 0.20 0.10 -0.57 17
West coast 2002 18 0.16 0.10 -0.59 18
West coast 2003 15 0.14 0.09 -0.58 15
West coast 2004 19 0.22 0.09 -0.60 19
West coast 2005 18 0.17 0.09 -0.68 17
West coast 2006 16 0.20 0.09 -0.75 15
West coast 2007 15 0.14 0.09 -0.76 14
West coast 2008 13 0.16 0.08 -0.79 12
West coast 2009 11 0.22 0.08 -0.85 10
West coast 2010 12 0.14 0.08 -0.76 12
West coast 2011 13 0.16 0.08 -0.81 12
West coast 2012 13 0.19 0.08 -0.44 13
West coast 2013 14 0.26 0.08 -0.47 14
West coast 2014 13 0.20 0.08 -0.65 13
West coast 2015 13 0.21 0.07 -0.56 13
West coast 2016 13 0.28 0.07 -0.48 13
West coast 2017 13 0.23 0.07 -0.49 12
West coast 2018 13 0.21 0.07 -0.59 13
West coast 2019 11 0.21 0.07 -0.46 11
West coast 2020 11 0.27 0.07 -0.71 10
West coast 2021 10 0.24 0.07 -0.61 10
West coast 2022 9.4 0.26 0.07 -0.72 9.0
West coast 2023 7.7 0.28 0.07 -0.54 6.5
West coast 2024 5.4 0.24 0.06 -0.65 5.1
Prairies 1990 -0.47 -5.9 0.19 -0.14 -6.3
Prairies 1991 -0.53 -11 0.18 -0.15 -12
Prairies 1992 -0.47 -9.3 0.24 -0.15 -9.7
Prairies 1993 -0.36 -5.6 0.22 -0.15 -5.9
Prairies 1994 -0.16 -11 0.21 -0.15 -12
Prairies 1995 -0.05 -11 0.21 -0.16 -11
Prairies 1996 0.00 -11 0.20 -0.16 -11
Prairies 1997 0.01 -16 0.19 -0.16 -16
Prairies 1998 -0.12 -11 0.18 -0.16 -11
Prairies 1999 0.00 -17 0.17 -0.16 -17
Prairies 2000 0.05 -20 0.17 -0.16 -20
Prairies 2001 -0.06 -16 0.16 -0.17 -16
Prairies 2002 0.03 -1.3 0.16 -0.17 -1.3
Prairies 2003 -0.03 -0.42 0.15 -0.17 -0.46
Prairies 2004 0.05 -22 0.15 -0.17 -22
Prairies 2005 0.16 -24 0.14 -0.18 -24
Prairies 2006 0.14 -25 0.14 -0.18 -25
Prairies 2007 0.12 -21 0.13 -0.18 -21
Prairies 2008 0.12 -21 0.13 -0.18 -21
Prairies 2009 0.14 -35 0.13 -0.18 -35
Prairies 2010 0.15 -25 0.12 -0.19 -25
Prairies 2011 0.13 -18 0.12 -0.17 -18
Prairies 2012 0.12 -22 0.12 -0.15 -22
Prairies 2013 0.05 -26 0.11 -0.11 -26
Prairies 2014 0.13 -39 0.11 -0.06 -39
Prairies 2015 0.15 -17 0.11 -0.01 -16
Prairies 2016 0.27 -18 0.10 -0.03 -18
Prairies 2017 0.45 -24 0.10 -0.05 -23
Prairies 2018 0.55 -22 0.10 -0.06 -21
Prairies 2019 0.54 -19 0.09 -0.13 -18
Prairies 2020 0.64 -19 0.09 -0.13 -19
Prairies 2021 0.37 -24 0.09 -0.13 -24
Prairies 2022 0.33 12 0.09 -0.14 12
Prairies 2023 0.13 -26 0.08 -0.14 -26
Prairies 2024 0.07 -12 0.08 -0.17 -12
Southeastern 1990 21 2.1 0.56 -0.52 24
Southeastern 1991 19 1.7 0.57 -0.51 21
Southeastern 1992 20 3.1 0.58 -0.55 23
Southeastern 1993 21 5.3 0.59 -0.64 26
Southeastern 1994 20 2.8 0.60 -0.64 23
Southeastern 1995 21 2.2 0.61 -0.67 23
Southeastern 1996 20 2.7 0.63 -0.64 23
Southeastern 1997 20 3.7 0.67 -0.68 23
Southeastern 1998 18 3.4 0.69 -0.54 21
Southeastern 1999 18 1.7 0.69 -0.46 20
Southeastern 2000 17 2.3 0.71 -0.49 20
Southeastern 2001 12 5.1 0.72 -0.50 17
Southeastern 2002 11 4.0 0.74 -0.56 15
Southeastern 2003 10 2.8 0.75 -0.54 13
Southeastern 2004 13 2.0 0.77 -0.50 16
Southeastern 2005 12 2.9 0.79 -0.63 15
Southeastern 2006 8.6 2.7 0.80 -0.66 11
Southeastern 2007 6.9 2.9 0.81 -0.67 9.9
Southeastern 2008 5.7 2.1 0.83 -0.67 8.0
Southeastern 2009 3.5 2.2 0.83 -0.68 5.9
Southeastern 2010 2.7 3.9 0.85 -0.73 6.7
Southeastern 2011 0.53 2.1 0.85 -0.73 2.8
Southeastern 2012 -1.7 3.2 0.86 -0.78 1.6
Southeastern 2013 -0.43 2.7 0.86 -0.71 2.4
Southeastern 2014 -0.20 2.8 0.86 -0.60 2.9
Southeastern 2015 0.21 6.0 0.87 -0.42 6.6
Southeastern 2016 -1.7 4.0 0.88 -0.43 2.7
Southeastern 2017 -2.2 3.5 0.90 -0.62 1.6
Southeastern 2018 -1.8 3.9 0.90 -0.64 2.4
Southeastern 2019 -4.5 4.2 0.91 -0.66 -0.07
Southeastern 2020 -4.6 5.1 0.93 -0.67 0.74
Southeastern 2021 -5.8 4.2 0.95 -0.69 -1.4
Southeastern 2022 -6.2 2.6 0.96 -0.68 -3.3
Southeastern 2023 -6.9 3.7 0.97 -0.71 -2.9
Southeastern 2024 -7.8 3.3 0.98 -0.70 -4.2

Note: Data are accurate to 2 significant figures. Net exchange is calculated by subtracting removals from emissions.

Download data file (Excel/CSV; 7.52 kB)
How this indicator was calculated

Note: Regions are based on the location of the human activities across the country. Forest sector regional estimates provided do not include the long-term impact of emissions from forest harvest or deforestation prior to 1990.
Source: Environment and Climate Change Canada (2026) National Inventory Report 1990-2024: Greenhouse gas sources and sinks in Canada.

The overall increase in removals of GHGs on the Prairies between 1990 and 2014 can be attributed to changes in agricultural land management practices, such as the adoption of conservation tillage, the proportion of annual and perennial crops, and the reduced use of summerfallow. These changes in land management decrease soil disturbance and thereby lower releases of carbon from the soil. In recent years, the decline in the proportion of perennial crops on the landscape and the rate of conservation tillage practices have been offset by increasing yields contributing to increased inputs of crop residue resulting in variable, but stable GHG removals for croplands as a whole. The transition from net removals to net emissions in 2022 stemmed largely from a major drought in 2021, reflecting how weather-related impacts can significantly affect crop production and reduce carbon inputs from residues. When crop yields decline due to drought, there are fewer plant residues to decompose and add organic carbon to the soil, leading to increased emissions instead of carbon storage (removals). The return to average yields in 2022 returned the soils to a carbon sink in 2023.

The increase in GHG emissions in the Boreal region and the shift from removals to emissions in the Mountain region are related to increased forest harvesting (in part to salvage timber from trees killed by the Mountain Pine Beetle and prevent its spread) as well as a reduction in net carbon removals from forests. The latter is due to insect infestations and fires in managed forests. The Boreal and the Mountain regions account for over 70% of the carbon transferred to harvested wood products. While timber harvesting transfers most of the carbon from stem wood to harvested wood products, it also results in emissions at the harvest site in the years immediately following the disturbance, primarily due to decomposition. The disturbances reduce the area of mature growing trees, which is already known to be slow in these regions and increase decomposition and salvage logging (the harvest of dead or dying standing trees). For more information, see the Forest sector in Land-based emissions and removals from human activities.

In the West Coast and Southeastern regions, forestry management practices (changes in harvest rates and forest regeneration) contributed to the reduction in emissions. That said, the West Coast still has the highest rate of carbon transfers to harvested wood products per hectare in Canada. In recent years, net GHG emissions have decreased in Southeastern region, due to forest growth.

Natural disturbances

Land-based GHG emissions and removals from natural disturbances

Forests remove carbon from the atmosphere as they grow and release it along with other GHGs when they decay after dying or burning in forest fires.

Key results

  • In 2024,
    • Emissions from wildfires (immediate emissions) contributed 350 megatonnes of carbon dioxide equivalent (Mt CO2 eq). These emissions were roughly 12 times higher than observed wildfire emissions since 1990
    • Emissions caused by insect infestations were 10 Mt CO2 eq
    • Emissions despite forest regrowth post-wildfires were 71 Mt CO2 eq
  • Since 2002, the net exchange from natural disturbances resulted in GHG emissions, ranging between 2.7 Mt CO2 eq and 1,000 Mt CO2 eq

Land-based greenhouse gas emissions and removals from natural disturbances in managed areas, Canada, 1990 to 2024

 Land-based greenhouse gas emissions and removals from natural disturbances in managed areas, Canada, 1990 to 2024 (see data table below for the long description)
Data table for the long description
Land-based greenhouse gas emissions and removals from natural disturbances in managed areas, Canada, 1990 to 2024
Year Wildfire – immediate emissions
(megatonnes of carbon dioxide equivalent)
Post wildfire
(megatonnes of carbon dioxide equivalent)
Insects
(megatonnes of carbon dioxide equivalent)
Net exchange
(megatonnes of carbon dioxide equivalent)
1990 29 -150 0.3 -130
1991 55 -150 0.4 -91
1992 12 -150 0.5 -140
1993 60 -150 0.5 -95
1994 67 -160 0.5 -89
1995 220 -140 0.6 78
1996 51 -130 0.6 -80
1997 14 -140 0.6 -120
1998 200 -130 1.0 80
1999 73 -120 3.5 -47
2000 10 -120 9.3 -100
2001 35 -120 17 -68
2002 130 -110 25 44
2003 95 -110 39 29
2004 150 -100 44 91
2005 55 -98 51 8.5
2006 76 -91 58 42
2007 74 -88 66 53
2008 38 -90 66 14
2009 58 -90 59 26
2010 110 -84 53 81
2011 130 -75 45 100
2012 110 -69 40 83
2013 57 -70 36 23
2014 170 -63 31 140
2015 250 -47 28 230
2016 101 -41 25 84
2017 210 -33 22 200
2018 240 -23 19 240
2019 140 -19 16 140
2020 13 -26 15 3.0
2021 280 -7.0 14 290
2022 86 -10 13 89
2023 950 56 11 1,000
2024 350 71 10 430

Note:Note: Data are accurate to 2 significant figures. Net exchange is calculated by subtracting removals from emissions.

Download data file (Excel/CSV; 2.05 kB)
How this indicator was calculated

Note: Wildfire emissions and removals are divided in 2 categories, (1) wildfire – immediate emissions and (2) post wildfire. Wildfire – immediate emissions include emissions from trees and soils from the burning of wildfires. Post wildfire includes emissions released by the decay of dead trees and soil organic matter and removals related to forest regeneration. Insect disturbances include emissions from the decay of organic matter and removals from natural regeneration.
Source: Environment and Climate Change Canada (2026) National Inventory Report 1990-2024: Greenhouse gas sources and sinks in Canada.

Natural disturbances are an important factor in determining whether forests remove or release GHGs each year. These disturbances contribute to immediate emissions (for example, from the burning of trees), as well as post-disturbance emissions and removals. Post-disturbance emissions are from the gradual decay of dead organic matter. Post-disturbance removals are related to the natural regeneration and regrowth of forests.

The variability in emissions and releases from natural disturbances can vary greatly from year to year. For example, emissions from managed lands were lower in 2020 than in adjacent years because of the smaller area burned.Footnote 5 However, since the mid-2000s, emissions from wildfires and insect disturbances have been increasing. In 2023, emissions from wildfires were greater than emissions from all other human emissions of GHGs in Canada. Additionally, severe insect infestations in the early 2000s are having an effect on today's net GHG exchange and are expected to influence GHG emissions over the next few decades.

About the indicator

About the indicator

What the indicator measures

The Land-based greenhouse gas emissions and removals indicator tracks exchanges of greenhouse gas (GHG) emissions and removals between the atmosphere and Canada's managed lands. Reported GHG emissions and removals are annual totals from:

  • Land use and land-use change activities
    • Forest sector (managed forested land, afforestation and harvested wood products)
    • Agricultural land (cropland, agricultural deforestation and agricultural grassland loss)
    • Wetlands (peat extraction, flooded land, wetland conversion and land conversion to wetland)
    • Settlements (developed land, wetland conversion and land conversion to settlement)
  • Natural disturbances (insect infestations and wildfires)

The indicator does not report emissions from Canadian economic sectors: oil and gas, transport, buildings, electricity, heavy industry, agriculture (such as fuel use, and crop and animal production) and waste. For information on those GHG emissions, refer to the Greenhouse gas emissions indicator.

Why this indicator is important

GHG emissions and their increasing concentrations in the atmosphere are having significant impacts on the environment, human health and the economy. Tracking the trends in Canada's land-based GHG emissions and removals provides a useful context for understanding how different management activities could reduce emissions and increase removals over time. This indicator could also help identify opportunities for mitigating the impacts of climate change and the potential for enhancing carbon sequestration.

The distinction between emissions and removals from human activities versus natural disturbances allows for a better understanding of emissions that could be directly managed in the near to medium term. The National Inventory Report has made this distinction since 2017 in the 2015 National Inventory Report.

Related indicators

The Greenhouse gas emissions indicators report trends in total anthropogenic (human-made) GHG emissions at the national level, per person and per unit gross domestic product, by province and territory and by economic sector.

The Global greenhouse gas emissions indicator provides a global perspective on Canada's share of global GHG emissions.

The Greenhouse gas emissions from a consumption perspective indicator shows the impact of Canada's consumption of goods and services, regardless of where they are produced, on the levels of carbon dioxide released into the atmosphere.

The Greenhouse gas emissions projections indicator provides an overview of Canada's projected GHG emissions up to 2035.

The Greenhouse gas emissions from large facilities indicator reports GHG emissions from the largest GHG emitters in Canada (industrial and other types of facilities).

The Greenhouse gas concentrations indicators present atmospheric concentrations as measured from sites in Canada and at a global scale for 2 greenhouse gases: carbon dioxide and methane.

The Forest management and disturbances indicator presents a series of measures covering timber harvest, forest disturbances, and forest regeneration.

Data sources and methods

Data sources and methods

Data sources

This indicator is developed using data from Canada's National Inventory Report and includes emissions and removals associated with natural disturbances and with land use, land-use change and forestry (LULUCF) activity on managed lands. Managed lands are defined by the Intergovernmental Panel on Climate Change (IPCC) as "land where human interventions and practices have been applied to perform production, ecological or social functions."Footnote 6 Information on the land category definition and representation of managed lands is available in Chapter 6 of the National Inventory Report.

Land-based greenhouse gas (GHG) emissions and removals include emissions and removals of carbon dioxide (CO2). It also includes emissions of methane (CH4), nitrous oxide (N2O), and indirect CO2 from the atmospheric oxidation of carbon monoxide (CO) due to controlled biomass burning; CH4 and N2O emissions from wetland drainage and rewetting due to peat extraction; and N2O released following land conversion to cropland.

More information

Data used to develop the land-based emission and removal estimates presented in the National Inventory Report are drawn from published and unpublished sources from various government departments, industry sources and scientific papers.

Land-based GHG emission estimates are provided at the national level, by sector and by region. Annual GHG emission estimates are updated each year; the most recent edition of the inventory reported estimates for the period from 1990 to 2024. Complete details of the temporal coverage for each data source used for the indicators can be found in Chapter 6 of the National Inventory Report. Details on the role of Forest harvesting on forest carbon emissions and removals can be found in Chapter 2, Section 2.3.4.1.1.

Preparation of the GHG inventory, including the land-based emission and removal estimates, takes almost 16 months from the end of the reporting year because of the time needed to collect, validate, calculate and interpret the data. In keeping with good practice guidance for managing national inventories, methods and data are improved on an on-going basis to reflect new knowledge and improved data or methods. Inventory estimates are prepared by Environment and Climate Change Canada's Pollutant Inventories and Reporting Division with input from numerous experts and scientists across Canada. Preliminary estimates and draft text are reviewed extensively by experts and officials, before they are finalized. The final report is submitted electronically to the United Nations Framework Convention on Climate Change (UNFCCC) no later than mid-April, as required.

Methods

Land-based GHG emissions and removals are quantified using methods that are consistent with an internationally agreed methodological framework set out in the 2006 IPCC Guidelines for National Greenhouse Gas Inventories and 2019 IPCC Refinement to the 2006 IPCC Guidelines for National Greenhouse Gas Inventories. The methodologies used to estimate emissions and removals are reviewed, updated and improved on a periodic basis. Collaborative work with sector experts from within and outside Environment and Climate Change Canada is undertaken to incorporate available expertise and the latest advancements in scientific knowledge. Further information on these methods is available through Environment and Climate Change Canada's National Inventory Report.

More information

Land-based GHG emissions and removals are reported in carbon dioxide equivalents (CO2 eq), determined by multiplying the amount of emissions of a particular GHG by the global warming potential of that gas. GHGs differ in their ability to absorb heat in the atmosphere due to their differing chemical properties and atmospheric lifetimes. For example, over a period of 100 years, the potential of methane to trap heat in the atmosphere is 28 times greater than that of carbon dioxide. Therefore, methane is considered to have a global warming potential of 28. The UNFCCC Reporting Guidelines (PDF; 259 KB) publish the global warming potentials and atmospheric lifetimes to be used for each GHG reported in national GHG inventories; these can be found in Table 1-1 of the National Inventory Report.

Areas within managed forests are subject to both forest management and natural disturbances. Emissions and removals from these areas are associated with human activities under specific circumstances. All stands harvested or that have been affected by stand-replacing natural disturbances in the past but have reached commercial maturity, or a minimum operable age (for a given region) are recognized to be under human influence. Commercially mature stands subject to natural disturbances causing less than or equal to 20% biomass mortality (for example some insects that cause defoliation but low mortality) remain associated with human activities. Large, uncontrollable natural disturbances (for example wildfires or insect outbreaks causing more than 20% biomass mortality) are recognized to result from natural occurrences and the associated emissions and removals are reflected in the natural disturbance category. See Annex 3.5 of the National Inventory Report for more information on the tracking and reporting of natural disturbances.Footnote 7

Spatial aggregation

Estimates for the land use, land-use change and forestry (LULUCF) sector in the National Inventory Report are provided for 18 reporting zones (Chapter 6, Figure 6-1 Canada's National Inventory Report). These reporting zones are similar to the ecozones of the National Ecological Framework, a hierarchical, spatially consistent national ecosystem classification.

In this indicator, the reporting zones were grouped into regional categories that better reflect trends in management practices. Table 1 shows the indicator regional categories and the corresponding National Inventory Report reporting zones.

Table 1. Indicator regional categories and National Inventory Report reporting zones
Indicator regional categories National Inventory Report reporting zones
Mountain Taiga Cordillera
Mountain Boreal Cordillera
Mountain Montane Cordillera
Boreal Taiga Plains
Boreal Taiga Shield West
Boreal Boreal Plains
Boreal Boreal Shield West
Boreal Hudson Plains
Boreal Boreal Shield East (excluding Newfoundland)
Boreal Taiga Shield East
West Coast Pacific Maritime
Prairies Subhumid Prairies
Prairies Semiarid Prairies
Southeastern Boreal Shield East (Newfoundland)
Southeastern Atlantic Maritime
Southeastern Mixedwood Plains
Not reported Arctic Cordillera
Not reported Northern Arctic
Not reported Southern Arctic

Land-based greenhouse gas emissions and removals by land use categories

In this indicator, calculated emissions and removals data from the National Inventory Report are grouped into 4 broad classes. Table 2 shows the categories of Land-based GHG emissions and removals reported in the indicator compared with those reported in the National Inventory Report.

Table 2. Land-based greenhouse gas emissions and removals categories
Land-based GHG emissions and removals categories reported in the sector Land-based GHG emissions and removals categories reported in the National Inventory Report
Forest sector Forest land
Forest sector Harvest wood products (HWP)
Agricultural land Cropland
Agricultural land Agricultural grassland
Wetlands Peat extraction and flooded lands
Settlements Settlements

Note: Definitions for land-use change and forest land as reported in the National Inventory Report are consistent with the International Panel on Climate Change land categories. Harvested wood product includes those that originate from forest trees, urban trees or agricultural land.

Recent changes

Recalculations occurred for the forest sector due to refinement of dead organic matter decay parameters through a Bayesian calibration of the Carbon Budget Model of the Canadian Forest Sector (CBM-CFS3) using National Forest Inventory plot data. Forest management activity data were also updated for clearcutting, commercial thinning, firewood collection and slash burning, including a -10% correction to 2023 harvest targets, resulting in a significant downward revision in 2023 emissions. For the Harvested Wood Products, methodological improvements to carbon allocation and residential bioenergy emission factors were implemented.

In Wetlands, updated activity data and emission factors, including improved representation of CH₄ and CO₂ and expanded reservoir coverage, resulted in revised emissions across the full time series. New estimates were also introduced for wetland conversion and management associated with resource extraction activities in Alberta’s Oil Sands Region.

Additional updates included revised manure management emission factors, inclusion of impurities in lime application in agricultural soils, and a correction to crop residue carbon inputs to soils, which resulted in slight upward revisions across the time series. Refer to Chapter 6 of the National Inventory Report for more information.

Caveats and limitations

The methodologies for compiling land-based GHG emissions and removals improve over time. As a result, the land-based GHG emissions and removals data reported in the indicator may be different from previously published estimates.

Harvested wood products are not limited to those that originate from forests and include those from urban trees and agricultural land. As such, the reported emissions from the forest sector may differ from the National Inventory Report. For more information, see Chapter 6.4 of the National Inventory Report.

Canada is a vast country with heterogeneous landscapes and climates. Factors such as geographic location, climatic conditions, plant species and age, and management activities all play a role in influencing the net amount of GHG that is removed or released back to the atmosphere from each location in Canada. The land-based emissions and removals data provide a simplified representation of the complex reality and may not account for all relevant ecological processes.

Current reporting of land-based GHG emissions and removals does not account for climate feedback other than what is captured through natural disturbances such as wildfires and insect infestations. Climate feedback mechanisms can either amplify (positive feedback) or diminish (negative feedback) the effects of a changing climate. For example, as rising concentrations of GHGs warm Earth's climate, permafrost begins to melt. This melting releases the organic carbon stored, contributing to GHG releases that cause more warming, which causes more melting, and so on, in a self reinforcing cycle.

For a complete discussion of the caveats and limitations with respect to land-based GHG emissions and removals data, refer to the methodological issues sections in Chapter 6 of Canada's National Inventory Report.

Resources

Resources

References

Environment and Climate Change Canada (2026) Canada's official greenhouse gas inventory. Retrieved June 25, 2026.

Intergovernmental Panel on Climate Change (2003) Good Practice Guidance for Land Use, Land-use Change and Forestry. Retrieved June 25, 2026.

Intergovernmental Panel on Climate Change (2006) 2006 IPCC Guidelines for National Greenhouse Gas Inventories, Vol. 4: Agriculture, Forestry and Other Land Use. Retrieved June 25, 2026.

Intergovernmental Panel on Climate Change (2019) 2019 Refinement to the 2006 IPCC Guidelines for National Greenhouse Gas Inventories, Vol. 4: Agriculture, Forestry and Other Land Use. Retrieved June 25, 2026.

Kurz WA, Hayne S, Fellows M, MacDonald JD, Metsaranta JM, Hafer M and Blain D (2018) Quantifying the impacts of human activities on reported greenhouse gas emissions and removals in Canada’s managed forest: conceptual framework and implementation. Canadian Journal of Forest Research 48: 1-14. Retrieved June 25, 2026.

Kurz WA, Hudson B, Neilson E, Fellows M, Hafer M and MacDonald JD (2024). Revised historic harvest data improve estimates of the impacts of human activities on reported greenhouse gas emissions and removals in Canada’s managed forest. Canadian Journal of Forest Research. Retrieved June 25, 2026.

Natural Resources Canada (2026) The State of Canada's Forests 2025. Retrieved June 25, 2026.

Warren FJ and Lemmen DS, editors (2014) Canada in a Changing Climate: Sector Perspectives on Impacts and Adaptation. Government of Canada, Ottawa, ON, 286p. Retrieved June 25, 2026.

Related information

Canada's Action on Climate Change
Climate Change
Land-based greenhouse gas emissions and removals infographic

Alternative format

Download the alternative format of the Land-based greenhouse gas emissions and removals indicator(PDF; 1.41 MB).

Infographic 
Infographic on Land-based greenhouse gas emissions and removals (see below for long description)
Long description 

The infographic presents information on the Land-based greenhouse gas emissions and removals indicator. A graphic is shown to represent the carbon cycle where carbon is absorbed from the atmosphere by trees, plants and soil through photosynthesis and released back into the atmosphere through burning and decomposition of soil and dead organic matter.

Greenhouse gases on Canada's managed lands in 2024:

  • Human activities accounted for net emissions of 4.7 Mt CO2 eq
  • Natural disturbances accounted for net emissions of 430 Mt CO2 eq

Emissions from human activities in 2024:

  • Forestry activities and tree growth contributed removals of 1.7 Mt CO2 eq
  • Agricultural land contributed removals of 3.4 Mt CO2 eq
  • Wetlands contributed emissions of 5.4 Mt CO2 eq
  • Urban lands and lands converted to settlements contributed emissions of 4.4 Mt CO2 eq

Emissions and removals from natural disturbances in 2024:

  • Wildfires contributed emissions of 350 Mt CO2 eq
  • Tree regrowth after wildfires contributed emissions of 71 Mt CO2 eq
  • Insect infestations contributed emissions of 10 Mt CO2 eq

In 2024, managed lands accounted for net emissions of about 430 Mt CO2 eq.

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2026-09-24

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