Abstract
Nitrogen is indispensable for global food production and ecosystem carbon sequestration, but excess nitrogen leads to water eutrophication, soil acidification and air pollution. Atmospheric nitrogen deposition is a key yet uncertain component of the biogeochemical cycle. Currently, global networks monitoring particulate nitrogen dry deposition rely mainly on measured concentrations and modelled dry deposition velocities, which remain poorly constrained. Here we develop a spatially explicit dataset by integrating observation-constrained size distribution and dry deposition mechanisms to re-evaluate atmospheric nitrogen deposition across China. We reveal that atmospheric chemistry models underestimate the particle size of fine-mode nitrogen-containing aerosols in China by more than twofold. Additionally, dry particle deposition velocity estimates with different mechanisms diverge by up to two orders of magnitude. Our corrections indicate that atmospheric chemistry models and China’s observation network underestimate particulate nitrogen dry deposition by 2–5 times. Furthermore, most Earth system models underestimate particulate dry deposition of ammonium, a major nitrogen species, by 31%–98%. By integrating these corrections into the Community Land Model, we demonstrate that the effect of nitrogen deposition on China’s terrestrial net ecosystem productivity may have been underestimated by 9%–13%. As China contributes nearly 20% of global nitrogen deposition, its impact on terrestrial carbon sinks and ecosystem health could be greater than previously recognized.
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Data availability
The underlying data employed in this study are available from sources cited in the main text and Supplementary Information or are provided in Supplementary Data. The CMIP6 data are available at https://aims2.llnl.gov/search/cmip6/. The revised map database is available via GitHub at https://github.com/huangynj/NCL-Chinamap.
Code availability
The default WRF-Chem model source code is freely available at https://www2.mmm.ucar.edu/wrf/users/download/get_sources_new.php. The CLM5 model code is available via Github at https://github.com/ESCOMP/CTSM/releases.
References
Gruber, N. & Galloway, J. N. An Earth-system perspective of the global nitrogen cycle. Nature 451, 293–296 (2008).
Houlton, B. Z. et al. A world of cobenefits: solving the global nitrogen challenge. Earthʼ s Future 7, 865–872 (2019).
Galloway, J. N. et al. Nitrogen cycles: past, present, and future. Biogeochemistry 70, 153–226 (2004).
Pan, D. et al. Regime shift in secondary inorganic aerosol formation and nitrogen deposition in the rural United States. Nat. Geosci. 17, 617–623 (2024).
Lamarque, J.-F. et al. Multi-model mean nitrogen and sulfur deposition from the Atmospheric Chemistry and Climate Model Intercomparison Project (ACCMIP): evaluation of historical and projected future changes. Atmos. Chem. Phys. 13, 7997–8018 (2013).
Liu, X. J. et al. Enhanced nitrogen deposition over China. Nature 494, 459–462 (2013).
Clark, C. M. & Tilman, D. Loss of plant species after chronic low-level nitrogen deposition to prairie grasslands. Nature 451, 712–715 (2008).
Lu, X., Mao, Q., Gilliam, F. S., Luo, Y. & Mo, J. Nitrogen deposition contributes to soil acidification in tropical ecosystems. Glob. Change Biol. 20, 3790–3801 (2014).
Maúre, E.dR., Terauchi, G., Ishizaka, J., Clinton, N. & DeWitt, M. Globally consistent assessment of coastal eutrophication. Nat. Commun. 12, 6142 (2021).
Reay, D. S., Dentener, F., Smith, P., Grace, J. & Feely, R. A. Global nitrogen deposition and carbon sinks. Nat. Geosci. 1, 430–437 (2008).
Lu, X. et al. Nitrogen deposition accelerates soil carbon sequestration in tropical forests. Proc. Natl Acad. Sci. USA 118, e2020790118 (2021).
Gong, C. et al. Global net climate effects of anthropogenic reactive nitrogen. Nature 632, 557–563 (2024).
Wang, R. et al. Global forest carbon uptake due to nitrogen and phosphorus deposition from 1850 to 2100. Glob. Change Biol. 23, 4854–4872 (2017).
Zhang, Q. et al. Atmospheric nitrogen deposition: a review of quantification methods and its spatial pattern derived from the global monitoring networks. Ecotoxilcol. Environ. Saf. 216, 112180 (2021).
Baker, A. R. et al. Observation- and model-based estimates of particulate dry nitrogen deposition to the oceans. Atmos. Chem. Phys. 17, 8189–8210 (2017).
Saylor, R. D. et al. The particle dry deposition component of total deposition from air quality models: right, wrong or uncertain?. Tellus Ser. B 71, 1550324 (2019).
Zhang, Y. et al. Long-term trends in total inorganic nitrogen and sulfur deposition in the US from 1990 to 2010. Atmos. Chem. Phys. 18, 9091–9106 (2018).
Xu, W., Zhang, L. & Liu, X. J. A database of atmospheric nitrogen concentration and deposition from the nationwide monitoring network in China. Sci. Data 6, 51 (2019).
Schwede, D. B. & Lear, G. G. A novel hybrid approach for estimating total deposition in the United States. Atmos. Environ. 92, 207–220 (2014).
Flechard, C. R. et al. Dry deposition of reactive nitrogen to European ecosystems: a comparison of inferential models across the NitroEurope network. Atmos. Chem. Phys. 11, 2703–2728 (2011).
Yu, G. R. et al. Stabilization of atmospheric nitrogen deposition in China over the past decade. Nat. Geosci. 12, 424–429 (2019).
Ackerman, D., Millet, D. B. & Chen, X. Global estimates of inorganic nitrogen deposition across four decades. Glob. Biogeochem. Cycle 33, 100–107 (2019).
Li, Q. K., Yang, Z., Li, X. D., Ding, S. Y. & Du, F. Seasonal characteristics of sulfate and nitrate in size-segregated particles in ammonia-poor and -rich atmospheres in Chengdu, Southwest China. Aerosol Air Qual. Res. 19, 2697–2706 (2019).
Ding, X. X. et al. Characteristics of size-resolved atmospheric inorganic and carbonaceous aerosols in urban Shanghai. Atmos. Environ. 167, 625–641 (2017).
Li, X. R. et al. Characterization of the size-segregated water-soluble inorganic ions in the Jing-Jin-Ji urban agglomeration: spatial/temporal variability, size distribution and sources. Atmos. Environ. 77, 250–259 (2013).
Nolte, C. G. et al. Evaluation of the Community Multiscale Air Quality (CMAQ) model v5.0 against size-resolved measurements of inorganic particle composition across sites in North America. Geosci. Model Dev. 8, 2877–2892 (2015).
Kelly, J. T. et al. Simulating the phase partitioning of NH3, HNO3, and HCl with size-resolved particles over northern Colorado in winter. Atmos. Environ. 131, 67–77 (2016).
Yao, X. H. & Zhang, L. Sulfate formation in atmospheric ultrafine particles at Canadian inland and coastal rural environments. J. Geophys. Res.: Atmos. 116, D10202 (2011).
Cabada, J. C. et al. Mass size distributions and size resolved chemical composition of fine particulate matter at the Pittsburgh supersite. Atmos. Environ. 38, 3127–3141 (2004).
Adams, P. J. & Seinfeld, J. H. Predicting global aerosol size distributions in general circulation models. J. Geophys. Res.: Atmos. 107, AAC 4-1–AAC 4-23 (2002).
Emerson, E. W. et al. Revisiting particle dry deposition and its role in radiative effect estimates. Proc. Natl Acad. Sci. USA 117, 26076–26082 (2020).
Zhang, Q. et al. Wintertime formation of large sulfate particles in China and implications for human health. Environ. Sci. Technol. 57, 20010–20023 (2023).
Wu, T. & Boor, B. E. Urban aerosol size distributions: a global perspective. Atmos. Chem. Phys. 21, 8883–8914 (2021).
Xiao, Q. et al. Tracking PM2.5 and O3 pollution and the related health burden in China 2013–2020. Environ. Sci. Technol. 56, 6922–6932 (2021).
Seinfeld, J. H. & Pandis, S. N. Atmospheric Chemistry and Physics: From Air Pollution to Climate Change (Wiley, 2016).
Zhai, S. X. et al. Control of particulate nitrate air pollution in China. Nat. Geosci. 14, 389–395 (2021).
Piao, S., He, Y., Wang, X. & Chen, F. Estimation of China’s terrestrial ecosystem carbon sink: methods, progress and prospects. Sci. China Earth Sci. 65, 641–651 (2022).
The Intergovernmental Panel on Climate Change. Climate Change 2021: The Physical Science Basis (eds Masson-Delmotte, V. et al.) (Cambridge Univ. Press, 2021).
Zaveri, R. A., Easter, R. C., Fast, J. D. & Peters, L. K. Model for Simulating Aerosol Interactions and Chemistry (MOSAIC). J. Geophys. Res.: Atmos. 113, D13204 (2008).
Xu, W. et al. Seasonal characterization of organic nitrogen in atmospheric aerosols using high resolution aerosol mass spectrometry in Beijing, China. ACS Earth Space Chem. 1, 673–682 (2017).
Peters, K. & Eiden, R. Modeling the dry deposition velocity of aerosol–particles to a spruce forest. Atmos. Environ. A 26, 2555–2564 (1992).
Binkowski, F. S. & Shankar, U. The regional particulate matter model .1. Model description and preliminary results. J. Geophys. Res.: Atmos. 100, 26191–26209 (1995).
Zhang, L. M., Gong, S. L., Padro, J. & Barrie, L. A size-segregated particle dry deposition scheme for an atmospheric aerosol module. Atmos. Environ. 35, 549–560 (2001).
Zhao, Y. H. et al. Atmospheric nitrogen deposition to China: a model analysis on nitrogen budget and critical load exceedance. Atmos. Environ. 153, 32–40 (2017).
Farmer, D. K., Boedicker, E. K. & DeBolt, H. M. Dry deposition of atmospheric aerosols: approaches, observations, and mechanisms. Annu. Rev. Phys. Chem. 72, 375–397 (2021).
Petroff, A. & Zhang, L. Development and validation of a size-resolved particle dry deposition scheme for application in aerosol transport models. Geosci. Model Dev. 3, 753–769 (2010).
Turnock, S. T. et al. Historical and future changes in air pollutants from CMIP6 models. Atmos. Chem. Phys. 20, 14547–14579 (2020).
Liu, L., Wen, Z., Liu, S., Zhang, X. & Liu, X. Decline in atmospheric nitrogen deposition in China between 2010 and 2020. Nat. Geosci. 17, 733–736 (2024).
Zhu, J. et al. Changing patterns of global nitrogen deposition driven by socio-economic development. Nat. Commun. 16, 46 (2025).
Chen, L. et al. MICS-Asia III: multi-model comparison and evaluation of aerosol over East Asia. Atmos. Chem. Phys. 19, 11911–11937 (2019).
Xie, X. et al. Modeling particulate nitrate in China: current findings and future directions. Environ. Int. 166, 107369 (2022).
Zeng, Y. et al. WRF-Chem v3.9 simulations of the East Asian dust storm in May 2017: modeling sensitivities to dust emission and dry deposition schemes. Geosci. Model Dev. 13, 2125–2147 (2020).
Emery, C. et al. Recommendations on statistics and benchmarks to assess photochemical model performance. J. Air Waste Manage. Assoc. 67, 582–598 (2017).
Huang, L. et al. Recommendations on benchmarks for numerical air quality model applications in China–part 1: PM 2.5 and chemical species. Atmos. Chem. Phys. 21, 2725–2743 (2021).
Zhang, X. et al. Ammonia emissions may be substantially underestimated in China. Environ. Sci. Technol. 51, 12089–12096 (2017).
Kong, L. et al. Improved inversion of monthly ammonia emissions in China based on the Chinese ammonia monitoring network and ensemble Kalman filter. Environ. Sci. Technol. 53, 12529–12538 (2019).
Flato, G. M. Earth system models: an overview. Wiley Interdiscip. Rev. Clim. Change 2, 783–800 (2011).
Galloway, J. N. et al. The nitrogen cascade. Bioscience 53, 341–356 (2003).
Fenn, M. E. et al. Ecological effects of nitrogen deposition in the western United States. Bioscience 53, 404–420 (2003).
Ran, L. S. et al. Substantial decrease in CO2 emissions from Chinese inland waters due to global change. Nat. Commun. 12, 1730 (2021).
Zhou, H. et al. Recovery of ecosystem productivity in China due to the Clean Air Action plan. Nat. Geosci. 17, 1233–1239 (2024).
Filbee-Dexter, K. et al. Carbon export from seaweed forests to deep ocean sinks. Nat. Geosci. 17, 552–559 (2024).
Campbell, A. D., Fatoyinbo, L., Goldberg, L. & Lagomasino, D. Global hotspots of salt marsh change and carbon emissions. Nature 612, 701–706 (2022).
Liu, X. Y., Tai, A. P. K. & Fung, K. M. Responses of surface ozone to future agricultural ammonia emissions and subsequent nitrogen deposition through terrestrial ecosystem changes. Atmos. Chem. Phys. 21, 17743–17758 (2021).
Shang, F. et al. Substantial nitrogen abatement accompanying decarbonization suppresses terrestrial carbon sinks in China. Nat. Commun. 15, 7738 (2024).
Friedlingstein, P. et al. Global carbon budget 2021. Earth Syst. Sci. Data 14, 1917–2005 (2022).
Zhu, H. et al. The response of nitrogen deposition in China to recent and future changes in anthropogenic emissions. J. Geophys. Res.: Atmos. 127, e2022JD037437 (2022).
Dynamic Projection for Emission in China (DPEC) v1.2 emission inventory. MEICModel http://meicmodel.org.cn/?page_id=1918&lang=en (2023).
Fu, Y. et al. Enhanced atmospheric nitrogen deposition at a rural site in northwest China from 2011 to 2018. Atmos. Res. 245, 105071 (2020).
Huang, X. J. et al. Seasonal variation and secondary formation of size-segregated aerosol water-soluble inorganic ions during pollution episodes in Beijing. Atmos. Res. 168, 70–79 (2016).
Yao, Q. et al. Seasonal variation and secondary formation of size-segregated aerosol water-soluble inorganic ions in a coast megacity of North China Plain. Environ. Sci. Pollut. Res. 27, 26750–26762 (2020).
China National Ambient Air Quality Standards(GB 3095-2012) (Ministry of Environmental Protection of the People’s Republic of China, 2012).
Shrivastava, M. et al. Urban pollution greatly enhances formation of natural aerosols over the Amazon rainforest. Nat. Commun. 10, 1046 (2019).
Oikawa, P. Y. et al. Unusually high soil nitrogen oxide emissions influence air quality in a high-temperature agricultural region. Nat. Commun. 6, 8753 (2015).
Liu, M. X. et al. Unexpected response of nitrogen deposition to nitrogen oxide controls and implications for land carbon sink. Nat. Commun. 13, 3126 (2022).
Liu, M. X. et al. Ammonia emission control in China would mitigate haze pollution and nitrogen deposition, but worsen acid rain. Proc. Natl Acad. Sci. USA 116, 7760–7765 (2019).
Ryu, Y. H. & Min, S. K. Improving wet and dry deposition of aerosols in WRF-Chem: updates to below-cloud scavenging and coarse-particle dry deposition. J. Adv. Model. Earth Syst. 14, e2021MS002792 (2022).
Buchholz,R. R., Emmons, L. K., Tilmes, S. & The CESM2 Development Team. CESM2.1/CAM-chem instantaneous output forboundary conditions. Subset used with Lat: 10 to 60, Lon: 60 to 140, December 2014–December 2015. UCAR/NCAR -Atmospheric Chemistry Observations and Modeling Laboratory https://doi.org/10.5065/NMP7-EP60 (2019).
Zaveri, R. A. & Peters, L. K. A new lumped structure photochemical mechanism for large-scale applications. J. Geophys. Res.: Atmos. 104, 30387–30415 (1999).
Su, J., Zhao, P. & Dong, Q. Chemical compositions and liquid water content of size-resolved aerosol in Beijing. Aerosol Air Qual. Res. 18, 680–692 (2018).
Ding, X. et al. Long-range and regional transported size-resolved atmospheric aerosols during summertime in urban Shanghai. Sci. Total Environ. 583, 334–343 (2017).
Zhao, P. S., Chen, Y. N. & Su, J. Size-resolved carbonaceous components and water-soluble ions measurements of ambient aerosol in Beijing. J. Environ. Sci. 54, 298–313 (2017).
Easter, R. C. et al. MIRAGE: model description and evaluation of aerosols and trace gases. J. Geophys. Res.: Atmos. 109, D20210 (2004).
Wesely, M. Parameterization of surface resistances to gaseous dry deposition in regional-scale numerical models. Atmos. Environ. 23, 1293–1304 (1989).
Li, H. Q., Zhang, H. L., Mamtimin, A., Fan, S. Y. & Ju, C. X. A new land-use dataset for the Weather Research and Forecasting (WRF) model. Atmosphere 11, 350 (2020).
Wang, Y., Zhang, Q., He, K., Zhang, Q. & Chai, L. Sulfate-nitrate-ammonium aerosols over China: response to 2000–2015 emission changes of sulfur dioxide, nitrogen oxides, and ammonia. Atmos. Chem. Phys. 13, 2635–2652 (2013).
Peckham, S. E. et al. WRF-Chem version 3.9.1.1 User’s Guide (NOAA, 2017).
Shu, Q., Koo, B., Yarwood, G. & Henderson, B. H. Strong influence of deposition and vertical mixing on secondary organic aerosol concentrations in CMAQ and CAMx. Atmos. Environ. 171, 317–329 (2017).
Wu, M. X. et al. Impacts of aerosol dry deposition on black carbon spatial distributions and radiative effects in the Community Atmosphere Model CAM5. J. Adv. Model. Earth Syst. 10, 1150–1171 (2018).
Timmermans, R. et al. Evaluation of modelled LOTOS-EUROS with observational based PM10 source attribution. Atmos. Environ.: X 14, 100173 (2022).
Slinn, W. G. N. Predictions for particle deposition to vegetative canopies. Atmos. Environ. 16, 1785–1794 (1982).
Slinn, S. A. & Slinn, W. G. N. Predictions for particle deposition on natural-waters. Atmos. Environ. 14, 1013–1016 (1980).
Slinn, W. Some approximations for the wet and dry removal of particles and gases from the atmosphere. Water Air Soil Pollut. 7, 513–543 (1977).
Bergametti, G. et al. Size-resolved dry deposition velocities of dust particles: in situ measurements and parameterizations testing. J. Geophys. Res.: Atmos. 123, 11080–11099 (2018).
Xu, W. et al. Spatial–temporal patterns of inorganic nitrogen air concentrations and deposition in eastern China. Atmos. Chem. Phys. 18, 10931–10954 (2018).
Zhang, Y., Yu, Q., Ma, W. & Chen, L. Atmospheric deposition of inorganic nitrogen to the eastern China seas and its implications to marine biogeochemistry. J. Geophys. Res.: Atmos. 115, D00K10 (2010).
Lawrence, D. M. et al. The Community Land Model version 5: description of new features, benchmarking, and impact of forcing uncertainty. J. Adv. Model. Earth Syst. 11, 4245–4287 (2019).
Davies-Barnard, T. et al. Nitrogen cycling in CMIP6 land surface models: progress and limitations. Biogeosciences 17, 5129–5148 (2020).
Bonan, G. B. et al. Model structure and climate data uncertainty in historical simulations of the terrestrial carbon cycle (1850–2014). Glob. Biogeochem. Cycles 33, 1310–1326 (2019).
Skamarock, W. C. A Description of the Advanced Research WRF Version 3 NCAR technical note 475 (NCAR, 2008).
Lombardozzi, D. L. et al. Simulating agriculture in the Community Land Model version 5. J. Geophys. Res.: Biogeosci. 125, e2019JG005529 (2020).
Wang, L., Wen, T.-X., Miao, H.-Y., Gao, W.-K. & Wang, Y.-S. Concentrations and size distributions of water-soluble inorganic ions in aerosol particles in Taiyuan, Shanxi. Environ. Sci. 37, 3249–3257 (2016).
Wang, L. Characteristics and Regional Distributions of Size-Segregated Water-Soluble Inorganic Ions in Atmospheric Particulate Matters in China. PhD thesis, Univ. of Chinese Academy of Sciences (2017).
Acknowledgements
This study was funded by the National Natural Science Foundation of China (grant numbers 42476127, 42577530 and 42521004); China Postdoctoral Science Foundation (2022M720005); Beijing Natural Science Foundation (8244068) and Science and Technology Projects of Xizang Autonomous Region, China (XZ202501ZY0091), and was supported by the High-Performance Computing Platform of Peking University and in part through research cyberinfrastructure resources and services provided by the Partnership for an Advanced Computing Environment (PACE) at the Georgia Institute of Technology, Atlanta, Georgia, USA. We also thank the public instrument platform of the College of Urban and Environmental Sciences at Peking University. Maodian Liu is also supported by the Fundamental Research Funds for the Central Universities, Peking University (7100604874). Y.-H.R. was funded by the National Research Foundation of Korea (NRF) grant funded by the Korean Government (MSIT) (RS-2023-00274625). H.L. was funded by the National Natural Science Foundation of China (42275166). We thank Y. Huang (IAP/CAS) for providing the map database (https://github.com/huangynj/NCL-Chinamap.git).
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Y.W., X.W., Maodian Liu and Q.Z. designed and led the research; X.W., Maodian Liu and Q.Z. acquired the funding needed to complete the study; Q.Z. and Maodian Liu performed the research and data collection; Y.-H.R. and Mingxu Liu contributed to the model configuration; H.L. contributed the updated land-use data; Y.W., Q.Z. and Maodian Liu made the data analysis and interpreted the results; Q.Z. and Maodian Liu wrote the original manuscript in close discussion with Y.W., S.W., J.L., S.T. and X.W. and all authors contributed to manuscript revision and completion.
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Extended data
Extended Data Fig. 1 Observed particle size distributions of NO3−, NH4+, and SO42− aerosols under different air pollution conditions in China.
The blue curves, ranging from light to dark, represent simulated results with pollution levels increasing from low to high, corresponding to the left y-axis. Similarly, the red curves, ranging from light to dark, depict observed results with increasing pollution levels from low to high, corresponding to the right y-axis. ‘SIM’ means simulations. ‘OBS’ means observations. ‘N’ means normal days. ‘LP’ means lightly polluted days. ‘HP’ means heavily polluted days. Daily air quality levels were classified based on average daily PM2.5 values. Some cities did not have heavily polluted days during the simulation period, resulting in the absence of some locations in SIM_HP figures. The observations here are obtained from previous publications102,103.
Extended Data Fig. 2 Changes in particulate nitrogen dry deposition over China constrained by observed particle size and new deposition mechanisms.
The spatial distribution of total particulate nitrogen dry deposition over China from the eight simulation experiments (a) and change in total particulate nitrogen dry deposition of the observation-derived experiment (Osize_E2020) compared with each other simulation experiment (b). Maps based on the original NCAR Command Language (NCL) map framework with updated boundary information derived from the National Catalogue Service for Geographic Information of China (http://www.webmap.cn/commres.do?method=result100W).
Extended Data Fig. 3 Changes in total nitrogen deposition over China constrained by observed particle size and new deposition mechanisms.
The spatial distribution of total nitrogen deposition over China from the eight simulation experiments (a) and change in total nitrogen deposition of the observation-derived experiment (Osize_E2020) compared with each other simulation experiment (b). Maps based on the original NCAR Command Language (NCL) map framework with updated boundary information derived from the National Catalogue Service for Geographic Information of China (http://www.webmap.cn/commres.do?method=result100W).
Extended Data Fig. 4 The comparison of net primary productivity (NPP) between simulations with the NASA NPP observations across China.
The gray line indicates the linear regression fit (mean estimate), and the gray shaded area denotes the 95% confidence interval for that regression line. Statistical metrics including R-squared (R2 = 0.74), root-mean-square deviation (RMSE = 155 gC m−2 yr−1) and fraction of simulation within a factor of two (FAC2 = 67%) are presented.
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Supplementary Texts 1–5, Figs. 1–6, Tables 1–9 and references.
Supplementary Data (download ZIP )
The datasets include: (1) additional observed NO3− and NH4+ concentrations in 2015, obtained from published literature used in this study. (2) Additional observed NO3− and NH4+ concentrations in 2014, obtained from published literature used in this study. (3) Simulated particulate nitrogen dry deposition in China by WRF-Chem under eight different model experiments in 2015. (4) Simulated total nitrogen deposition in China by WRF-Chem under Osize_E2020 in 2015.
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Zhang, Q., Wang, Y., Liu, M. et al. Underestimation of particulate dry nitrogen deposition in China. Nat. Geosci. 19, 137–144 (2026). https://doi.org/10.1038/s41561-025-01873-3
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DOI: https://doi.org/10.1038/s41561-025-01873-3


