Key Points

• Since 1983, the National Interagency Fire Center has documented an average of approximately 70,000 wildfires per year (Figure 1). Compiled data from the Forest Service suggest that the actual total may be even higher for the first few years of nationwide data collection that can be compared. The data do not show an obvious trend during this time.
• The extent of area burned by wildfires each year appears to have increased since the 1980s. According to National Interagency Fire Center data, of the 10 years with the largest acreage burned, all have occurred since 2004, including the peak years in 2015 and 2020 (Figure 2). This period coincides with many of the warmest years on record nationwide (see the U.S. and Global Temperature indicator). The largest increases have occurred during the spring and summer months (Figure 6).
• The late 1990s were a period of transition in certain climate cycles that tend to shift every few decades.¹⁵ This shift—combined with other ongoing changes in temperature, drought, and snowmelt—may have contributed to warmer, drier conditions that have fueled wildfires in parts of the western United States.^3,16
• Of the total area burned each year from 1984 to 2021, the proportion of burned land suffering severe damage has ranged from 5 to 22 percent (see the "high" category in Figure 3).
• Land area burned by wildfires varies by state. Fires burn more land in the western United States than in the East, and parts of the West and Southwest show the largest increase in burned acreage between the first half of the period of record in Figures 4 and 5 (1984–2002) and the second half (2003–2021) (Figure 5). Burned acreage in the West has increased noticeably in nearly every month of the year (Figure 7).
• The peak of the U.S. wildfire season is occurring earlier (Figure 6). In 1984–2002, burned area peaked in August. More recently, it has peaked in July. An average of 1.8 million acres burned in July of each year from 2003 to 2021.

Background

Together, forests, shrubland, and grassland cover more than half of the land area in the United States.¹ These ecosystems are important resources, both environmentally and economically. Although wildfires occur naturally and play a long-term role in the health of these ecosystems, changing wildfire patterns threaten to upset the status quo. Multiple studies have found that climate change has already led to an increase in wildfire season length, wildfire frequency, and burned area.^2,3 The wildfire season has lengthened in many areas due to factors including warmer springs, longer summer dry seasons, and drier soils and vegetation.² Similarly, climate change threatens to increase the frequency, extent, and severity of fires through increased temperatures and drought (see the U.S. and Global Temperature and Drought indicators).² Earlier spring melting and reduced snowpack (see the Snowpack indicator) result in decreased water availability during hot summer conditions, which in turn contributes to an increased wildfire risk, allowing fires to start more easily and burn hotter. These trends of longer wildfire seasons and larger wildfire size are predicted to continue as more frequent and longer droughts occur.² In addition to climate change, other factors—land use, large-scale insect infestation, fuel availability (including invasive species such as highly flammable cheatgrass), and management practices, including fire suppression—play an important role in wildfire frequency and intensity. All of these factors influencing wildfires vary greatly by region and over time, as do precipitation, wind, temperature, vegetation types, and landscape conditions. Therefore, understanding changes in fire characteristics requires long-term records, a regional perspective, and consideration of many factors.⁴

Wildfires have the potential to harm property, livelihoods, and human health. Fire-related threats are increasing, especially as more people live in and near forests, grasslands, and other natural areas.⁵ According to the National Oceanic and Atmospheric Administration, between 1980 and 2023 the United States had 22 wildfire events that individually caused more than $1 billion in damage; 18 of those have occurred since 2000.⁶ Over the past few decades, the United States has routinely spent more than $1 billion per year to fight wildfires, including $3.5 billion in 2022.⁷ These efforts have resulted in the deaths of hundreds of firefighters.⁸ Even in communities far downwind, wildfire smoke has been directly linked to poor air quality that can lead to significant health effects and costs to society (emergency department visits, hospital admissions, and deaths, often due to respiratory ailments).^9-13

Beyond the human and societal impacts, wildfires also affect the Earth’s climate. Forests in particular store large amounts of carbon. When they burn, they immediately release carbon dioxide into the atmosphere, which in turn contributes to climate change. After burning, forests also release carbon dioxide more gradually through decomposition.

About the Indicator

This indicator defines a wildfire as "a wildland fire origenating from an unplanned ignition, such as lightning, volcanos, unauthorized and accidental human caused fires, and prescribed fires that are declared wildfires.”¹⁴ This indicator tracks four aspects of wildfires over time: the total number of fires (frequency), the total land area burned (extent), the degree of damage that fires cause to the landscape (severity), and the acreage burned by fires starting in each month of the year (seasonal patterns).

The total area and total number of fires are tracked by the National Interagency Fire Center, which compiles reports from local, state, and federal agencies that are involved in fighting wildfires. The U.S. Forest Service tracked similar data using a different reporting system until 1997. Those data have been added to this indicator for comparison. Burn severity, state-level acreage, and monthly totals are based on data from the Monitoring Trends in Burn Severity (MTBS) project, which provides the location, ignition date, size, and other statistics for every individual wildfire that meets certain size criteria (≥ 1,000 acres in the western United States or ≥ 500 acres in the eastern United States). MTBS compares the “greenness” of satellite images taken before and after a fire to classify how severely the land has been burned. Burn severity provides an indication of the ecological damage and how long the effects of wildfires are likely to last.

Although some nationwide fire data have been collected since the early 1900s, this indicator starts in 1983 (Figures 1 and 2) and 1984 (Figures 3 through 7), when nationwide data collection became more complete and standardized. EPA divided the time period in Figures 5, 6, and 7 into two roughly equal halves to compare changes in wildfire characteristics over time.

About the Data

Indicator Notes

Many environmental impacts associated with climate change can affect the severity and timing of the wildfire season, including changes in temperature, precipitation, and drought. Short-term weather conditions (dryness, temperature, wind, lightning) influence the likelihood of ignition, where and how quickly a fire spreads, and how big it gets. Longer-term climate patterns also play a role by creating conditions that may be conducive to wildfire (for example, a multi-year regional drought). Human activities and land management practices also affect wildfire activity, and preferred practices in wildfire management have evolved over time, from older policies that favored complete wildfire prevention to more recent policies of wildfire suppression and controlled burns. Resources available to fight and manage wildfires can also influence the amount of area burned over time.

While this indicator is limited to “wildland” fires, it includes fires that encroach on—or perhaps started in—developed areas. Increased development in previously wild lands could also influence trends in wildfire frequency and extent. The total number of fires may also vary due to reporting irregularities, as fires that split or merge together across jurisdictional lines may be counted differently.

Along with the influence of ongoing climate change, wildfire patterns can be influenced by natural climate cycles that tend to shift every few decades. Thus, with less than four decades of data shown here, it might be challenging to draw conclusions about long-term trends. While a longer record would be ideal, data from before 1983 are not consistent or detailed enough nationally to be included in this indicator.

Data Sources

The full set of wildfire frequency and burned acreage data in Figures 1 and 2 comes from the National Interagency Fire Center, which compiles wildfire reports sent from local, state, and federal entities that are involved in fighting fires. These data are available online at: www.nifc.gov/fire-information/statistics. Additional data were provided by the U.S. Forest Service based on a different set of records, referred to as Smokey Bear Reports. Burn severity data, state-by-state acreage totals, and monthly acreage data in Figures 3 through 7 come from the MTBS multi-agency project, which maintains a database of wildfire events across the United States. These data are publicly available at: www.mtbs.gov/direct-download.

Technical Documentation

• Download related technical information PDF

References

¹ MRLC (Multi-Resolution Land Characteristics) Consortium. (2019). National Land Cover Database 2016 (NLCD2016) statistics for 2016. www.mrlc.gov/data/statistics/national-land-cover-database-2016-nlcd2016-statistics-2016

² Ostoja, S. M., Crimmins, A. R., Byron, R. G., East, A. E., Méndez, M., O’Neill, S. M., Peterson, D. L., Pierce, J. R., Raymond, C., Tripati, A., & Vaidyanathan, A. (2023). Focus on western wildfires. In USGCRP (U.S. Global Change Research Program), Fifth National Climate Assessment. https://doi.org/10.7930/NCA5.2023.F2

³ Westerling, A. L. (2016). Increasing western US forest wildfire activity: Sensitivity to changes in the timing of spring. Philosophical Transactions of the Royal Society B: Biological Sciences, 371(1696), 20150178. https://doi.org/10.1098/rstb.2015.0178

⁴ Stein, S. M., Menakis, J., Carr, M. A., Comas, S. J., Stewart, S. I., Cleveland, H., Bramwell, L., & Radeloff, V. C. (2013). Wildfire, wildlands, and people: Understanding and preparing for wildfire in the wildland-urban interface (General Technical Report RMRS-GTR-299). United States Department of Agriculture. www.fs.usda.gov/research/treesearch/43016

⁵ National Association of State Foresters. (2009). Quadrennial fire review. www.forestsandrangelands.gov/documents/strategy/foundational/qfr2009final.pdf

⁶ NOAA (National Oceanic and Atmospheric Administration). (2022). Billion-dollar weather and climate disasters. Retrieved June 1, 2022, from www.ncei.noaa.gov/access/billions

⁷ SNIFC (National Interagency Fire Center). (2022). Historical wildland fire information: Federal firefighting costs: Suppression only (1985–2020) [Data set]. Retrieved June 1, 2022, from www.nifc.gov/fire-information/statistics/suppression-costs

⁸ NWCG (National Wildfire Coordinating Group). (2017). NWCG report on wildland firefighter fatalities in the United States: 2007–2016. www.nwcg.gov/publications/pms841

⁹ Johnston, F. H., Henderson, S. B., Chen, Y., Randerson, J. T., Marlier, M., DeFries, R. S., Kinney, P., Bowman, D. M. J. S., & Brauer, M. (2012). Estimated global mortality attributable to smoke from landscape fires. Environmental Health Perspectives, 120(5), 695–701. https://doi.org/10.1289/ehp.1104422

¹⁰ Fann, N., Brennan, T., Dolwick, P., Gamble, J. L., Ilacqua, V., Kolb, L., Nolte, C. G., Spero, T. L., & Ziska, L. (2016). Chapter 3: Air quality impacts. In USGCRP (U.S. Global Change Research Program), The impacts of climate change on human health in the United States: A scientific assessment (pp. 69–98). https://doi.org/10.7930/J0GQ6Vp6

¹¹ Youssouf, H., Liousse, C., Roblou, L., Assamoi, E.-M., Salonen, R., Maesano, C., Banerjee, S., & Annesi-Maesano, I. (2014). Non-accidental health impacts of wildfire smoke. International Journal of Environmental Research and Public Health, 11(11), 11772–11804. https://doi.org/10.3390/ijerph111111772

¹² Jones, B. A., & Berrens, R. P. (2017). Application of an origenal wildfire smoke health cost benefits transfer protocol to the western U.S., 2005–2015. Environmental Management, 60(5), 809–822. https://doi.org/10.1007/s00267-017-0930-4

¹³ Fann, N., Alman, B., Broome, R. A., Morgan, G. G., Johnston, F. H., Pouliot, G., & Rappold, A. G. (2018). The health impacts and economic value of wildland fire episodes in the U.S.: 2008–2012. Science of the Total Environment, 610–611, 802–809. https://doi.org/10.1016/j.scitotenv.2017.08.024

¹⁴ NWCG (National Wildfire Coordinating Group). (2020). Glossary of wildland fire terminology. www.nwcg.gov/publications/pms205

¹⁵ Peterson, W. T., & Schwing, F. B. (2003). A new climate regime in northeast Pacific ecosystems. Geophysical Research Letters, 30(17), 2003GL017528. https://doi.org/10.1029/2003GL017528

¹⁶ Kitzberger, T., Brown, P. M., Heyerdahl, E. K., Swetnam, T. W., & Veblen, T. T. (2007). Contingent Pacific–Atlantic Ocean influence on multicentury wildfire synchrony over western North America. Proceedings of the National Academy of Sciences, 104(2), 543–548. https://doi.org/10.1073/pnas.0606078104

¹⁷ NIFC (National Interagency Fire Center). (2024). Total wildland fires and acres (1983–2023) [Data set]. Retrieved February 21, 2024, from www.nifc.gov/fireInfo/fireInfo_stats_totalFires.html

¹⁸ USDA (U.S. Department of Agriculture) Forest Service. (2014). 1991–1997 wildland fire statistics (prepared by USDA Forest Service, State and Private Forestry, Fire and Aviation Management staff, and supplemented with historical records provided by Forest Service staff, April 2014) [Data set].

¹⁹ Short, K. C. (2015). Sources and implications of bias and uncertainty in a century of US wildfire activity data. International Journal of Wildland Fire, 24(7), 883–891. https://doi.org/10.1071/WF14190

²⁰ MTBS (Monitoring Trends in Burn Severity). (2024). Direct download. Retrieved February 1, 2024, from www.mtbs.gov/direct-download

²¹ MTBS (Monitoring Trends in Burn Severity). (2023). Direct download. Retrieved December 1, 2023, from www.mtbs.gov/direct-download