Rapid nitrate reduction produces pulsed NO and N2O emissions following wetting of dryland soils

Soil drying and wetting cycles can produce pulses of nitric oxide (NO) and nitrous oxide (N 2 O) emissions with substantial effects on both regional air quality and Earth’s climate. While pulsed production of N emissions is ubiquitous across ecosystems, the processes governing pulse magnitude and ti...

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Veröffentlicht in:Biogeochemistry 2022-03, Vol.158 (2), p.233-250
Hauptverfasser: Krichels, Alexander H., Homyak, Peter M., Aronson, Emma L., Sickman, James O., Botthoff, Jon, Shulman, Hannah, Piper, Stephanie, Andrews, Holly M., Jenerette, G. Darrel
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container_end_page 250
container_issue 2
container_start_page 233
container_title Biogeochemistry
container_volume 158
creator Krichels, Alexander H.
Homyak, Peter M.
Aronson, Emma L.
Sickman, James O.
Botthoff, Jon
Shulman, Hannah
Piper, Stephanie
Andrews, Holly M.
Jenerette, G. Darrel
description Soil drying and wetting cycles can produce pulses of nitric oxide (NO) and nitrous oxide (N 2 O) emissions with substantial effects on both regional air quality and Earth’s climate. While pulsed production of N emissions is ubiquitous across ecosystems, the processes governing pulse magnitude and timing remain unclear. We studied the processes producing pulsed NO and N 2 O emissions at two contrasting drylands, desert and chaparral, where despite the hot and dry conditions known to limit biological processes, some of the highest NO and N 2 O flux rates have been measured. We measured N 2 O and NO emissions every 30 min for 24 h after wetting soils with isotopically-enriched nitrate and ammonium solutions to determine production pathways and their timing. Nitrate was reduced to N 2 O within 15 min of wetting, with emissions exceeding 1000 ng N–N 2 O m −2  s −1 and returning to background levels within four hours, but the pulse magnitude did not increase in proportion to the amount of ammonium or nitrate added. In contrast to N 2 O, NO was emitted over 24 h and increased in proportion to ammonium addition, exceeding 600 ng N–NO m −2  s −1 in desert and chaparral soils. Isotope tracers suggest that both ammonia oxidation and nitrate reduction produced NO. Taken together, our measurements demonstrate that nitrate can be reduced within minutes of wetting summer-dry desert soils to produce large N 2 O emission pulses and that multiple processes contribute to long-lasting NO emissions. These mechanisms represent substantial pathways of ecosystem N loss that also contribute to regional air quality and global climate dynamics.
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Darrel</creator><creatorcontrib>Krichels, Alexander H. ; Homyak, Peter M. ; Aronson, Emma L. ; Sickman, James O. ; Botthoff, Jon ; Shulman, Hannah ; Piper, Stephanie ; Andrews, Holly M. ; Jenerette, G. Darrel</creatorcontrib><description>Soil drying and wetting cycles can produce pulses of nitric oxide (NO) and nitrous oxide (N 2 O) emissions with substantial effects on both regional air quality and Earth’s climate. While pulsed production of N emissions is ubiquitous across ecosystems, the processes governing pulse magnitude and timing remain unclear. We studied the processes producing pulsed NO and N 2 O emissions at two contrasting drylands, desert and chaparral, where despite the hot and dry conditions known to limit biological processes, some of the highest NO and N 2 O flux rates have been measured. We measured N 2 O and NO emissions every 30 min for 24 h after wetting soils with isotopically-enriched nitrate and ammonium solutions to determine production pathways and their timing. Nitrate was reduced to N 2 O within 15 min of wetting, with emissions exceeding 1000 ng N–N 2 O m −2  s −1 and returning to background levels within four hours, but the pulse magnitude did not increase in proportion to the amount of ammonium or nitrate added. In contrast to N 2 O, NO was emitted over 24 h and increased in proportion to ammonium addition, exceeding 600 ng N–NO m −2  s −1 in desert and chaparral soils. Isotope tracers suggest that both ammonia oxidation and nitrate reduction produced NO. Taken together, our measurements demonstrate that nitrate can be reduced within minutes of wetting summer-dry desert soils to produce large N 2 O emission pulses and that multiple processes contribute to long-lasting NO emissions. 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Darrel</creatorcontrib><title>Rapid nitrate reduction produces pulsed NO and N2O emissions following wetting of dryland soils</title><title>Biogeochemistry</title><addtitle>Biogeochemistry</addtitle><description>Soil drying and wetting cycles can produce pulses of nitric oxide (NO) and nitrous oxide (N 2 O) emissions with substantial effects on both regional air quality and Earth’s climate. While pulsed production of N emissions is ubiquitous across ecosystems, the processes governing pulse magnitude and timing remain unclear. We studied the processes producing pulsed NO and N 2 O emissions at two contrasting drylands, desert and chaparral, where despite the hot and dry conditions known to limit biological processes, some of the highest NO and N 2 O flux rates have been measured. We measured N 2 O and NO emissions every 30 min for 24 h after wetting soils with isotopically-enriched nitrate and ammonium solutions to determine production pathways and their timing. 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Darrel</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Rapid nitrate reduction produces pulsed NO and N2O emissions following wetting of dryland soils</atitle><jtitle>Biogeochemistry</jtitle><stitle>Biogeochemistry</stitle><date>2022-03-01</date><risdate>2022</risdate><volume>158</volume><issue>2</issue><spage>233</spage><epage>250</epage><pages>233-250</pages><issn>0168-2563</issn><eissn>1573-515X</eissn><abstract>Soil drying and wetting cycles can produce pulses of nitric oxide (NO) and nitrous oxide (N 2 O) emissions with substantial effects on both regional air quality and Earth’s climate. While pulsed production of N emissions is ubiquitous across ecosystems, the processes governing pulse magnitude and timing remain unclear. We studied the processes producing pulsed NO and N 2 O emissions at two contrasting drylands, desert and chaparral, where despite the hot and dry conditions known to limit biological processes, some of the highest NO and N 2 O flux rates have been measured. We measured N 2 O and NO emissions every 30 min for 24 h after wetting soils with isotopically-enriched nitrate and ammonium solutions to determine production pathways and their timing. Nitrate was reduced to N 2 O within 15 min of wetting, with emissions exceeding 1000 ng N–N 2 O m −2  s −1 and returning to background levels within four hours, but the pulse magnitude did not increase in proportion to the amount of ammonium or nitrate added. In contrast to N 2 O, NO was emitted over 24 h and increased in proportion to ammonium addition, exceeding 600 ng N–NO m −2  s −1 in desert and chaparral soils. Isotope tracers suggest that both ammonia oxidation and nitrate reduction produced NO. 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subjects Air quality
Ammonia
Ammonium
Ammonium compounds
Arid zones
Background levels
Biogeosciences
Biological activity
Chaparral
Climate
Desert soils
Deserts
Drying
Earth and Environmental Science
Earth Sciences
Ecosystems
Emission measurements
Emissions
Environmental Chemistry
Global climate
Isotopes
Life Sciences
Nitrate reduction
Nitrates
Nitric oxide
Nitrous oxide
Oxidation
Reduction
Sandy soils
Soil
Soils
Tracers
Wetting
title Rapid nitrate reduction produces pulsed NO and N2O emissions following wetting of dryland soils
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