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 in | Biogeosciences Vol. 20; no. 5; pp. 971 - 995 |
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Main Authors | , , , , , , , , , , , , |
Format | Journal Article |
Language | English |
Published |
Germany
Copernicus GmbH
09.03.2023
Copernicus Publications |
Subjects | |
Online Access | Get full text |
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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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Bibliography: | ObjectType-Article-1 SourceType-Scholarly Journals-1 ObjectType-Feature-2 content type line 23 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 |