4.6 Article

Balancing watershed nitrogen budgets: accounting for biogenic gases in streams

期刊

BIOGEOCHEMISTRY
卷 127, 期 2-3, 页码 231-253

出版社

SPRINGER
DOI: 10.1007/s10533-015-0177-1

关键词

Denitrification; Greenhouse gases; Headwater streams; Nitrogen; Radon; Watershed budget

资金

  1. NSF (DEB) [0919181, 0919141, 1252923]
  2. Maryland Water Resources Research Center
  3. Izaak Walton League-Midshore Chapter
  4. Horn Point Laboratory Graduate Student Fellowship
  5. Division Of Environmental Biology
  6. Direct For Biological Sciences [1252923, GRANTS:13775313, 0919181, 919141] Funding Source: National Science Foundation
  7. Division Of Environmental Biology
  8. Direct For Biological Sciences [1325553] Funding Source: National Science Foundation

向作者/读者索取更多资源

Denitrification is critical for removal of reactive nitrogen (Nr) from ecosystems. However, measuring realistic, scalable rates and understanding the role of denitrification and other dissimilatory processes in watershed nitrogen (N) budgets remains a significant challenge in biogeochemistry. In this study, we focused on the stream reach and network scale in three Mid-Atlantic coastal plain watersheds. We applied open channel methods to measure biogenic N-2 and N2O gas fluxes derived from both in-stream and terrestrial nitrogen processing. A large portion of biogenic N-2 flux through streams (33-100 %, mean = 74 %) was a result of groundwater delivery of biogenic N-2 with the remaining portion due to in-stream N-2 production. In contrast, N2O was largely produced in-stream, with groundwater delivery contributing on average 12 % of the total biogenic N2O flux. We scaled these measurements across one stream network and compared them to hydrologic Nr export and net anthropogenic N inputs (NANI) to a 4.8 km(2) watershed. The N budget revealed that, during the study period, the biogenic N-2 flux through streams was comparable to the difference between NANI and hydrologic Nr export (i.e. the missing N). This study provides a methodological and conceptual framework for incorporating terrestrial and in-stream derived biogenic N gas fluxes into watershed N budgets and supports the hypothesis that denitrification is the primary fate of NANI that is not exported in streamflow.

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