Atmospheric deposition of reactive nitrogen to a deciduous forest in the southern Appalachian Mountains

Assessing nutrient critical load exceedances requires complete and accurate atmospheric deposition budgets for reactive nitrogen (N ). The exceedance is the total amount of N deposited to the ecosystem in excess of the critical load, which is the amount of N input below which harmful effects do not...

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Published inBiogeosciences Vol. 20; no. 5; pp. 971 - 995
Main Authors Walker, John T, Chen, Xi, Wu, Zhiyong, Schwede, Donna, Daly, Ryan, Djurkovic, Aleksandra, Oishi, A Christopher, Edgerton, Eric, Bash, Jesse, Knoepp, Jennifer, Puchalski, Melissa, Iiames, John, Miniat, Chelcy F
Format Journal Article
LanguageEnglish
Published Germany Copernicus GmbH 09.03.2023
Copernicus Publications
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Summary:Assessing nutrient critical load exceedances requires complete and accurate atmospheric deposition budgets for reactive nitrogen (N ). The exceedance is the total amount of N deposited to the ecosystem in excess of the critical load, which is the amount of N input below which harmful effects do not occur. Total deposition includes all forms of N (i.e., organic and inorganic) deposited to the ecosystem by wet and dry pathways. Here we present results from the Southern Appalachian Nitrogen Deposition Study (SANDS), in which a combination of measurements and field-scale modeling was used to develop a complete annual N deposition budget for a deciduous forest at the Coweeta Hydrologic Laboratory. Wet deposition of ammonium, nitrate, nitrite, and bulk organic N were measured directly. The dry deposited N fraction was estimated using a bidirectional resistance-based model driven with speciated measurements of N air concentrations (e.g., ammonia, ammonium aerosol, nitric acid, nitrate aerosol, bulk organic N in aerosol, total alkyl nitrates, and total peroxy nitrates), micrometeorology, canopy structure, and biogeochemistry. Total annual deposition was ~6.7 kg N ha yr , which is on the upper end of N critical load estimates recently developed for similar ecosystems in the nearby Great Smoky Mountains National Park. Of the total (wet + dry) budget, 51.1% was contributed by reduced forms of N , with oxidized and organic forms contributing ~41.3% and 7.6%, respectively. Our results indicate that reductions in deposition would be needed to achieve the lowest estimates (~3.0 kg N ha yr ) of N critical loads in southern Appalachian forests.
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Author contributions. JTW: conceptualization, formal analysis, methodology, funding acquisition, project administration, validation, visualization, writing. XC: formal analysis, investigation, methodology, validation, writing. ZW: formal analysis, investigation, methodology, software validation, writing. DS: investigation, formal analysis. RD: investigation, formal analysis, validation. AD: data curation, investigation, methodology, resources. ACO: conceptualization, formal analysis, methodology, validation. EE: data curation, funding acquisition, formal analysis, methodology, validation, resources. JB: formal analysis, methodology, software. JK: data curation, investigation. MP: conceptualization, funding acquisition, resources. JI: formal analysis, investigation, writing. CFM: conceptualization, funding acquisition, resources, writing.
now at: RTI International, Durham, NC, USA
retired
now at: U.S. Department of Agriculture, Forest Service, Albuquerque, NM, USA
now at: U.S. Environmental Protection Agency, Office of Air Quality Planning and Standards, Durham, NC, USA
now at: Boulder A.I.R. LLC, Boulder, CO, USA
ISSN:1726-4170
1726-4189
1726-4189
DOI:10.5194/bg-20-971-2023