Abstract
Nitrogen fixation can be a dominant flux of nitrogen (N) input providing up to 97 % of new N into some terrestrial and up to 82 % into some aquatic ecosystems, yet N2 fixation is rarely considered in the context of other N cycling fluxes. We compared N2 fixation with dissolved inorganic N (DIN) uptake fluxes in several streams. We measured N2 fixation in nine streams in Grand Teton National Park, Wyoming, USA and surrounding areas and we compared our estimates to the ammonium (NH+4)uptake, nitrate (NO-3) uptake, and denitrification estimates from the literature for those streams. N2 fixation was negligible or below detection in the four streams with NO-3 concentrations >20 μg NO-3 -N L−1. N2 fixation exceeded NO-3 uptake in two of the nine streams and NH+4 uptake in one stream. To further examine the relationship between N2 fixation and DIN uptake, we chose Ditch Creek, which is a low-N stream (<5 µg DIN-N L−1) with high rates of N2 fixation. We measured N2 fixation, NH+4 uptake, and NO-3 uptake biweekly throughout one summer. In Ditch Creek, DIN uptake exceeded N2 fixation at the beginning and end of the summer, but from July to the beginning of September N2 fixation was up to eight times greater than DIN uptake. The epilithic biofilm in Ditch Creek accumulated 1.5 g N m−2 throughout the summer, and N2 fixation may have contributed up to 73 % of that accumulation. Ditch Creek N2 fixation surpassed denitrification for both Ditch Creek and many streams. N2 fixation can be a dominant flux in low-N stream ecosystems.
| Original language | English |
|---|---|
| Pages (from-to) | 537-549 |
| Number of pages | 13 |
| Journal | Biogeochemistry |
| Volume | 121 |
| Issue number | 3 |
| DOIs | |
| State | Published - Nov 19 2014 |
Funding
Acknowledgments We thank Marley Vaughn for her help in the field and laboratory, Patricia Colberg for lending us her gas chromatograph (GC), Norbert Swoboda-Colberg for kindly setting up the GC at a remote field station, Hank Harlow for support at the UW-NPS field station, and Sue O’Ney at Grand Teton National Park for permitting and support. Bill Resor facilitated our work on Snake River Ranch. Jennifer Tank provided comments and suggestions on our approach. We thank Mike Marshall, Ben Koch, Lusha Tronstad, Erin Hotchkiss, and Amber Ulseth who were very supportive throughout this work. We also thank Carlos Martinez del Rio, James Lovvorn, William Reiners, Timothy Robinson, and 4 anonymous reviewers for comments and suggestions that greatly improved earlier drafts of this manuscript. The Wyoming Water Development Commission, United States Geological Survey, and National Science Foundation (NSF) grant DEB 0111410 funded this work. L.K. was supported by the University of Wyoming, NSF EPSCoR, and NSF GK-12 DGE0841298 fellowships.
| Funders | Funder number |
|---|---|
| DEB 0111410 | |
| University of Wyoming | |
| GK-12 DGE0841298 |
UN SDGs
This output contributes to the following UN Sustainable Development Goals (SDGs)
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SDG 15 Life on Land
Keywords
- Algal assemblage dynamics
- Ammonium uptake
- N cycling
- Nitrate uptake
- Nitrogen fixation
- Streams
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