Abstract
Wildfire activity has increased in the USA and is projected to accelerate under future climate change1,2,3. However, our understanding of the impacts of climate change on wildfire activity, smoke and health outcomes remains highly uncertain because of the difficulty of modelling the causal chain from climate to wildfire to air pollution and health. Here we quantify the mortality burden in the USA due to wildfire smoke fine particulate matter (PM2.5) under climate change. We construct an ensemble of statistical and machine learning models that link climate to wildfire smoke PM2.5 and empirically estimate smoke PM2.5–mortality relationships using data on all recorded deaths in the USA. We project that smoke PM2.5 could result in 71,420 excess deaths (95% confidence interval: 34,930–98,430) per year by 2050 under a high-warming scenario (shared socioeconomic pathway scenario 3-7.0, SSP3-7.0)—a 73% increase relative to the estimated 2011–2020 average annual excess deaths from smoke. Cumulative excess deaths from smoke PM2.5 could reach 1.9 million between 2026 and 2055. We find evidence for mortality impacts of smoke PM2.5 that last up to 3 years after exposure. When monetized, climate-driven smoke deaths result in economic damages that exceed existing estimates of climate-driven damages from all other causes combined in the USA4,5. Our research suggests that the health impacts of climate-driven wildfire smoke could be among the most important and costly consequences of a warming climate in the USA.
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Data availability
Data needed to replicate results and main text figures are available in a public repository at Zenodo92 (https://doi.org/10.5281/zenodo.16855665), except for county-level mortality data for low-population counties, which were obtained through application to the National Center for Health Statistics. Although we cannot share the full mortality data that we used in the analysis, we released a dataset that allows replication of our smoke–mortality model using public mortality data derived from CDC WONDER.
Code availability
R code to replicate results and main text figures is available at Zenodo92 (https://doi.org/10.5281/zenodo.16855665).
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Acknowledgements
We thank A. Wilson for helping process mortality data; Y. Ma and K. Chen for sharing their smoke mortality estimates for comparison; A. van Donkelaar for helping with dataset of total PM2.5 concentrations; seminar participants at Stanford University, Harvard University and the Brookhaven National Laboratory for comments; and the Keck Foundation for funding. M.Q. acknowledges the support from the planetary health fellowship at Stanford’s Center for Innovation in Global Health, and Minghua Zhang faculty career catalyst award from Stony Brook University. M.L.C. was supported by an Environmental Fellowship at the Harvard University Center for the Environment. R.J. acknowledges support for this work from NIH grant R01HD104835 and the Ruth L. Kirschstein National Research Service Award grant 5T32HS026128-07. N.S.D. acknowledges support from Stanford University. Some of the computing for this project was performed on the Stanford Sherlock cluster, and we thank Stanford University and the Stanford Research Computing Center for providing computational resources and support that contributed to these research results. NCEP North American Regional Reanalysis (NARR) data were provided by the NOAA PSL from their website (https://psl.noaa.gov).
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M.Q. and M.B. designed the study. M.Q. led the smoke projection modelling with inputs from all of the authors. M.Q., J.L. and R.J. led the statistical and machine learning modelling of fire emissions. M.Q., S.H.-N., C.F.G. and M.L.C. led the health impacts analysis. M.Q. and M.B. led the writing of the manuscript. M.Q., J.L., C.F.G., R.J., M.K., M.L.C., J.W., Y.X., M.L., M.V.K., S.H.-N., N.S.D. and M.B contributed to interpretation of results and reviewed the manuscripts.
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Extended data figures and tables
Extended Data Fig. 1 Future smoke contribution from different fire regions.
Source-receptor matrix of the contributions from fire emissions from the five source regions (x-axis) to population-weighted smoke PM2.5 concentrations in nine receptor regions across the contiguous US (y-axis). The plot shows the contributions in 2046–2055 averaged over all GCMS under the SSP3-7.0 scenario.
Extended Data Fig. 2 Historical and projected dry matter (DM) emissions.
Historical annual average emissions in 2001–2021 and projected annual emissions (2046–2055) under the SSP3-7.0 scenario in the eastern US (top), Canada and Alaska (middle), and Mexico (bottom). Projected emissions are first stochastically downscaled from regional emissions predictions and then averaged over 40 simulated downscaling estimates.
Extended Data Fig. 3 Illustration of the stochastic downscaling approach using the western US as an example.
Historical annual average emissions in 2001–2021 from GFED4s, and projected annual emissions averaged between 2046–2055 under the SSP3-7.0 scenario at the grid level. The “static” panel shows the results derived from the static downscaling method, which applies a common ratio to the historical emission pattern to match the future projected emissions. The “stochastic” panel shows our main stochastic downscaling method, which generates the same total emissions as the static method regionally but allows for the possibility that grids that have never burned could burn. Projected emissions are first stochastically downscaled from regional emissions predictions and then averaged over 40 simulated downscaling estimates (six are shown here for the illustration purpose).
Extended Data Fig. 4 Estimated annual excess deaths due to smoke PM2.5 using alternative exposure-response functions.
Panel A: results estimated using alternative smoke-mortality models (averaged over 2011–2020). In addition to our main model (grey bar), we estimate a model that uses the public mortality data from CDC WONDER, a model that additionally includes year 2020 in the regressions, a model that follows similar specification from Ma et al., 2024 (i.e. a monthly model with alternative bin specifications and 12-month moving average of smoke PM2.5 concentration), and models which calculates the number of months or the number of days in a year that fall in different smoke bins to represent different temporal aggregations. The bars show mean values of bootstrapped estimates, and the whiskers show bootstrapped 95% confidence intervals (500 bootstraps). Panel B: results estimated using published exposure-response functions that link total PM2.5 to mortality. Note the results here are estimated using lag 0 model and all-ages group, to match earlier work.
Extended Data Fig. 5 Cumulative effects of smoke on mortality across different lag years.
Panel A: aggregated coefficients for each smoke bin across different lag years, representing the cumulative effects of smoke exposure on mortality in the same year and subsequent years. Panel B: estimated mortality due to annual smoke PM2.5 under historical (2011–2020) and future scenarios (2046–2055). The plot shows the same-year mortality due to smoke (in the case of lag 0), and cumulative mortality (lag 0-1,…,lag 0-4). The bars show mean values of bootstrapped estimates, and the whiskers show bootstrapped 95% confidence intervals (500 bootstraps). We report results from “lag 0-1” model as our main estimates.
Extended Data Fig. 6 Estimated excess deaths due to smoke PM2.5 under the historical, SSP1-2.6, and SSP3-7.0 scenarios due to annual smoke exposure (lag 0-1).
The top panels show estimates at the county level. The bottom panels show estimates at the state level.
Extended Data Fig. 7 Uncertainty in projected annual smoke PM2.5 concentration (Panel A) and mortality (Panel B).
The red dashed line shows the main estimate. The solid bar shows the 10th and 90th percentile, and the black line shows the 2.5th and 97.5th percentile. Uncertainty from “climate projection” is calculated using the percentiles of 28 GCMs. Uncertainty from “climate-fire model” and “fire-smoke model” is calculated using bootstrap procedures performed on the climate-fire and fire-smoke models. Uncertainty from “emission downscaling” shows the range of smoke and mortality estimated across 40 different downscaling estimates. Uncertainty from “smoke-mortality function” is calculated using bootstrap procedures performed on the smoke-mortality response functions. The combined uncertainty is quantified using a Monte-Carlo simulation approach, where we randomly sample 500 combinations of GCMs, climate-fire models, downscaling estimates, and fire-smoke models, and smoke-mortality functions.
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Qiu, M., Li, J., Gould, C.F. et al. Wildfire smoke exposure and mortality burden in the USA under climate change. Nature 647, 935–943 (2025). https://doi.org/10.1038/s41586-025-09611-w
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DOI: https://doi.org/10.1038/s41586-025-09611-w
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