Details
Originalsprache | Englisch |
---|---|
Aufsatznummer | 727 |
Fachzeitschrift | Frontiers in Microbiology |
Jahrgang | 7 |
Ausgabenummer | JUN |
Publikationsstatus | Veröffentlicht - 2016 |
Abstract
Wetlands represent sources or sinks of the greenhouse gas nitrous oxide (N 2O). The acidic fen Schlöppnerbrunnen emits denitrification derived N 2O and is also capable of N 2O consumption. Global warming is predicted to cause more extreme weather events in future years, including prolonged drought periods as well as heavy rainfall events, which may result in flooding. Thus, the effects of prolonged drought and flooding events on the abundance, community composition, and activity of fen denitrifiers were investigated in manipulation experiments. The water table in the fen was experimentally lowered for 8 weeks in 2008 and raised for 5.5 months in 2009 on three treatment plots, while three plots were left untreated and served as controls. In situ N 2O fluxes were rather unaffected by the drought treatment and were marginally increased by the flooding treatment. Samples were taken before and after treatment in both years. The structural gene markers narG and nosZ were used to assess possible changes in the nitrate reducer and denitrifier community in response to water table manipulations. Detected copy numbers of narG and nosZ were essentially unaffected by the experimental drought and flooding. Terminal restriction fragment length polymorphism (TRFLP) patterns of narG and nosZ were similar before and after experimental drought or experimental flooding, indicating a stable nitrate reducer and denitrifier community in the fen. However, certain TRFs of narG and nosZ transcripts responded to experimental drought or flooding. Nitrate-dependent Michaelis-Menten kinetics were assessed in anoxic microcosms with peat samples taken before and 6 months after the onset of experimental flooding. Maximal reaction velocities vmax were higher after than before flooding in samples from treament but not in those from control plots taken at the same time. The ratio of N 2O to N 2O + N 2 was lower in soil from treatment plots after flooding than in soil from control plots, suggesting mitigation of N 2O emissions by increased N 2O-reduction rates after flooding. N 2O was consumed to subatmospheric levels in all microcosms after flooding. The collective data indicate that water table manipulations had only minor effects on in situ N 2O fluxes, denitrifier abundance, and denitrifier community composition of the acidic fen, while active subpopulations of denitrifiers changed in response to water table manipulations, suggesting functionally redundant subpopulations occupying distinct ecological niches in the fen.
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- Immunologie und Mikrobiologie (insg.)
- Mikrobiologie
- Medizin (insg.)
- Mikrobiologie (medizinisch)
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in: Frontiers in Microbiology, Jahrgang 7, Nr. JUN, 727, 2016.
Publikation: Beitrag in Fachzeitschrift › Artikel › Forschung › Peer-Review
}
TY - JOUR
T1 - Drying-Rewetting and Flooding Impact Denitrifier Activity Rather than Community Structure in a Moderately Acidic Fen
AU - Palmer, K.
AU - Köpp, J.
AU - Gebauer, G.
AU - Horn, M. A.
N1 - Publisher Copyright: © 2016 Palmer, Köpp, Gebauer and Horn. Copyright: Copyright 2017 Elsevier B.V., All rights reserved.
PY - 2016
Y1 - 2016
N2 - Wetlands represent sources or sinks of the greenhouse gas nitrous oxide (N 2O). The acidic fen Schlöppnerbrunnen emits denitrification derived N 2O and is also capable of N 2O consumption. Global warming is predicted to cause more extreme weather events in future years, including prolonged drought periods as well as heavy rainfall events, which may result in flooding. Thus, the effects of prolonged drought and flooding events on the abundance, community composition, and activity of fen denitrifiers were investigated in manipulation experiments. The water table in the fen was experimentally lowered for 8 weeks in 2008 and raised for 5.5 months in 2009 on three treatment plots, while three plots were left untreated and served as controls. In situ N 2O fluxes were rather unaffected by the drought treatment and were marginally increased by the flooding treatment. Samples were taken before and after treatment in both years. The structural gene markers narG and nosZ were used to assess possible changes in the nitrate reducer and denitrifier community in response to water table manipulations. Detected copy numbers of narG and nosZ were essentially unaffected by the experimental drought and flooding. Terminal restriction fragment length polymorphism (TRFLP) patterns of narG and nosZ were similar before and after experimental drought or experimental flooding, indicating a stable nitrate reducer and denitrifier community in the fen. However, certain TRFs of narG and nosZ transcripts responded to experimental drought or flooding. Nitrate-dependent Michaelis-Menten kinetics were assessed in anoxic microcosms with peat samples taken before and 6 months after the onset of experimental flooding. Maximal reaction velocities vmax were higher after than before flooding in samples from treament but not in those from control plots taken at the same time. The ratio of N 2O to N 2O + N 2 was lower in soil from treatment plots after flooding than in soil from control plots, suggesting mitigation of N 2O emissions by increased N 2O-reduction rates after flooding. N 2O was consumed to subatmospheric levels in all microcosms after flooding. The collective data indicate that water table manipulations had only minor effects on in situ N 2O fluxes, denitrifier abundance, and denitrifier community composition of the acidic fen, while active subpopulations of denitrifiers changed in response to water table manipulations, suggesting functionally redundant subpopulations occupying distinct ecological niches in the fen.
AB - Wetlands represent sources or sinks of the greenhouse gas nitrous oxide (N 2O). The acidic fen Schlöppnerbrunnen emits denitrification derived N 2O and is also capable of N 2O consumption. Global warming is predicted to cause more extreme weather events in future years, including prolonged drought periods as well as heavy rainfall events, which may result in flooding. Thus, the effects of prolonged drought and flooding events on the abundance, community composition, and activity of fen denitrifiers were investigated in manipulation experiments. The water table in the fen was experimentally lowered for 8 weeks in 2008 and raised for 5.5 months in 2009 on three treatment plots, while three plots were left untreated and served as controls. In situ N 2O fluxes were rather unaffected by the drought treatment and were marginally increased by the flooding treatment. Samples were taken before and after treatment in both years. The structural gene markers narG and nosZ were used to assess possible changes in the nitrate reducer and denitrifier community in response to water table manipulations. Detected copy numbers of narG and nosZ were essentially unaffected by the experimental drought and flooding. Terminal restriction fragment length polymorphism (TRFLP) patterns of narG and nosZ were similar before and after experimental drought or experimental flooding, indicating a stable nitrate reducer and denitrifier community in the fen. However, certain TRFs of narG and nosZ transcripts responded to experimental drought or flooding. Nitrate-dependent Michaelis-Menten kinetics were assessed in anoxic microcosms with peat samples taken before and 6 months after the onset of experimental flooding. Maximal reaction velocities vmax were higher after than before flooding in samples from treament but not in those from control plots taken at the same time. The ratio of N 2O to N 2O + N 2 was lower in soil from treatment plots after flooding than in soil from control plots, suggesting mitigation of N 2O emissions by increased N 2O-reduction rates after flooding. N 2O was consumed to subatmospheric levels in all microcosms after flooding. The collective data indicate that water table manipulations had only minor effects on in situ N 2O fluxes, denitrifier abundance, and denitrifier community composition of the acidic fen, while active subpopulations of denitrifiers changed in response to water table manipulations, suggesting functionally redundant subpopulations occupying distinct ecological niches in the fen.
KW - Climate change
KW - Greenhouse gases
KW - Structural (functional) genes
KW - Water table manipulation
KW - Wetlands
UR - http://www.scopus.com/inward/record.url?scp=84980041330&partnerID=8YFLogxK
U2 - 10.3389/fmicb.2016.00727
DO - 10.3389/fmicb.2016.00727
M3 - Article
VL - 7
JO - Frontiers in Microbiology
JF - Frontiers in Microbiology
SN - 1664-302X
IS - JUN
M1 - 727
ER -