(Editor’s note: This article was updated to adjust figures.)
Forest and range fires (also called wildfires or wildland fires) destroy property, timber, grass, wildlife habitat, affect water quality with increased runoff and soil erosion, and emit large amounts of greenhouse gases (GHG). The effects of fires are not always negative, and controlled prescribed fires can prevent large destructive fires by removing fuels. Fire can also improve forest and range conditions by controlling invasive weeds and conifer encroachment, enhancing forage quality increasing plant diversity and improving wildlife habitat.
However, in many cases, preventing and controlling forest and range fires is necessary to prevent large scale destruction and the loss of timber value. Between 2001 and 2021, 46 million to 61 million acres of timber in forests burned worldwide. This timber would be worth about $45-77 billion at the 2021 average price of $0.27/board foot (see the References at wlj.net). Local estimates for the northwest U.S. are about 1,000 to 2,000 board feet (1 to 2 mbf) per acre and $0.30 to $0.40 per board foot of timber. Loss of timber on an acre in the northwest can be estimated as a loss of about $300-800 per acre.
The U.S. Forest Service reports that in the U.S., wildfires and prescribed fires are a significant source of GHG (e.g., carbon dioxide, or CO2, and methane, or CH4) and carbon particle emissions. Exposure to smoke is also a hazard to public health and firefighters (see the References). GHG are thought to be the primary cause of climate change. I’ve written before about the amounts of CO2 emitted from forest fires (WLJ March 28, 2025) and how timber harvest can prevent forests from burning and lock up CO2 in wood products and regenerating trees. Locking up CO2 is called sequestering in climate change research. Forests currently sequester 12.4% of the U.S. GHG emissions and good forest management can substantially increase this.
My calculations indicated that about 225 (200 to 250) tons of CO2 per acre of forest can be locked up in harvested wood products. Another 123 tons of CO2 per acre can be locked up in new tree regeneration after about 60 years. This indicates that timber harvest followed by regenerating trees can lock up about 350 (325 to 375) tons of CO2 per acre. The amount of CO2 per acre will vary among locations, tree species and age, and other factors, but it’s clear that lots of CO2 can be locked up in wood products and tree regeneration.
Consider estimates on a larger scale. The Department of the Interior (DOI) keeps track of fires in the U.S. In the 42 years from 1983 to 2024, there was a total of 2.9 million fires, with an average of about 70,000 fires per year in the U.S. These fires include 217 million* total acres burned with an average of 5.2 million acres burned per year. (*Updated on Nov. 13 to 217 million acres from the originally noted 2.2 million acres).
The DOI report doesn’t specify how much of the 5 million acres burned per year area is forest, so I’ll do some rough calculations. Let’s say half of the 5 million acres is forest: 2.5 million acres of trees/year burned or killed and decayed. Using my estimate of 225 tons CO2/acre in timber: 225 tons/acre multiplied by 2.5 million acres = 563 million tons of CO2/year emitted from fires nationwide. It’s important to acknowledge that this is a gross estimate because of my assumption that half of burned area is forest and the amount of CO2/acre will depend on many factors.
Regardless, forest fires release a large amount of CO2 and other GHG. Total CO2 emissions in the U.S. in 2024 from residential, commercial, industry, transportation and electric power (not fires) was 5.3 billion tons. A total of 563 million tons emitted by fires divided by 5.3 billion tons of human emissions equals 0.11. This means that forest fires emitted 11% as much CO2 as human emissions in the U.S. in 2024. Limiting emissions from fires should be a priority for climate change mitigation.
Why is this issue important? Preventing the loss of human life, property, valuable timber and other negative effects of fires is the most obvious reason. But the potential to harvest timber while at the same time locking up substantial amounts of GHG are also obvious and complementary management objectives.
Climate change and reducing GHG continues to be a big environmental issue, as do environmental opposition and lawsuits to stop timber harvest, particularly on Forest Service and Bureau of Land Management lands. Using timber harvest to improve forest management and to lock up CO2 should not be opposed by environmentalists. It should be endorsed as a way to better manage forests and help mitigate climate change. — Matt Cronin, WLJ columnist
(Matt Cronin is a biologist with Northwest Biology and Forestry Company LLC in Bozeman, MT, and a teaching professor at Montana State University. He may be contacted at croninm@aol.com.)
References and notes
Notes: The amount of CO2 (tons) in harvested and regenerating trees is calculated with a conversion of 6.1 tons of green wood per thousand board feet; minus the weight of the water content of green wood (0.4 times green wood weight); times the fraction of wood that is carbon (0.5 times the dry wood weight); plus the weight of the oxygen combined with the weight of the tree carbon to form CO2 (3.67 times the weight of carbon in the tree).
A board foot is a piece of wood 1 inch by 1 foot by 1 foot. A board foot is a unit of measurement for lumber that represents a volume of 1 square foot that is1 inch thick. To calculate board feet, you can use the formula:
Board Feet = (Thickness in inches × Width in inches × Length in feet) / 12.
This measurement is commonly used in the lumber industry to quantify the amount of wood in a given piece of lumber.
Smoke Emissions | US Forest Service Research and Development
Wildfires and Acres | National Interagency Fire Center DOI website
Bousfield, G.C, D.B. Lindenmayer and D.P. Edwards. 2023. Substantial and increasing global losses of timber-producing forest due to wildfires. Nature Geoscience Volume 16: 1145–1150. Substantial and increasing global losses of timber-producing forest due to wildfires | Nature Geoscience
U.S. Energy Information Administration – EIA – Independent Statistics and Analysis
The Energy in Wildfires: The Western United States
Can Mowing Substitute for Fire in Semiarid Grassland? Vermeire et al. 2020
untitled Vermeire et al 2014 Semiarid Rangeland Is Resilient to Summer Fire and Postfire Grazing Utilization
WLJ articles on Forests, fires, logging, and climate change:
June 17, 2022 Resource Science: Timber and fire | Top Headlines | wlj.net
November 11, 2022 Resource Science: Logging, forest fires and greenhouse gas emissions | Resource Science | wlj.net
December 22, 2023 Resource Science: A new category of forests – Old growth | Resource Science | wlj.net
August 9, 2024 Resource Science: Forests and climate change | | wlj.net
October 16, 2024 Resource Science: How much CO2 is in trees? | Western Livestock Journal
March, 28, 2025 Resource Science: Forest fires, CO2 in harvested and regenerated trees | Western Livestock Journal
Forestry references
University of Montana Bureau of Business and Economic Research 2025. Montana State timber harvest total 2019 to 2023. Bureau of Business and Economic Research.
Memorandum of Understanding Between the American Loggers Council and the USDA, Forest Service. July 2024. American Loggers Council Signs Historic Memorandum of Understanding with the USDA Forest Service — American Loggers Council I The National Voice for Loggers (amloggers.com)
Kolb, P. 2024. Forest resilience, restoration, and collaboration. Montana State University Extension Forestry. Forest Resilience, Resistance, Restoration and Collaboration – MSU Extension | Montana State University
Mann, C.N. and H.H. Lysons. 1972. A method of estimating log weights. U.S. Forest Service Research Paper PNW-138, Portland, Oregon.
Stage, A.R, D.L. Renner, and R.C. Chapman. 1988. Select yield tables for plantations and natural stands in inland Northwest forests. USDA Forest Service, Research Paper INT-394, November 1988.
Brown, J.K., J.A. Kendall Snell, and D.L. Bunnell. 1977. Handbook for predicting slash weight of western conifers. U.S. Forest Service General Technical Report INT-37, July, 1977. Ogden, Utah.
McArdle, R.E., W.H. Meyer, and D. Bruce. 1930, revised 1949 and 1961. The yield of Douglas fir in the Pacific Northwest. USDA Technical Bulletin No. 201.
Domke et al. 2023. Greenhouse gas emissions and removals from forest land, woodlands, urban trees, and harvested wood products in the United States, 1990-2021. Resource Bulletin WO-101. Washington, DC: U.S. Department of Agriculture, Forest Service, Washington Office. 10 p. Greenhouse Gas Emissions and Removals From Forest Land, Woodlands, Urban Trees, and Harvested Wood Products in the United States, 1990–2021 (usda.gov)
U.S. Forest Service. 2021. FS-1189c | December 2021. Forest Carbon Status and Trends. R&D Hot Topic: Forest Carbon Status and Trends (usda.gov)
Global maps of twenty-first century forest carbon fluxes | Nature Climate Change
Environment: How much carbon do forests absorb? | World Economic Forum (weforum.org)
Wood Species – Moisture Content and Weight (engineeringtoolbox.com)
Wood and Moisture | The Wood Database (wood-database.com)
Calculating the Carbon Stored in Wood Products – WoodWorks | Wood Products Council
FTM: The Fire and Tree Mortality Database | US Forest Service Research and Development (usda.gov)





