New Zealand Journal of Agricultural Research · 2014 · 33 citations · 30 references
AgricultureEnvironmental SciencesSoil SciencesPasture MonitoringSoil MicrobiologySoil ScienceGreenhouse Gas ProductionNitrogen CycleNitrogen CyclingNitrogen OxidesSoil Nitrogen SensingAnaerobic Soil ConditionsDenitrificationDenitrification ProcessesNitrogen Cycling In PasturesNitrous OxideNitrous Oxide FormationRelative Abundance AnalysisTemperature Effects
Denitrification results in the formation of two gaseous end‐products: radiatively active greenhouse gas nitrous oxide (N 2 O) and radiatively inert di‐nitrogen (N 2 ). Measuring N 2 produced by soil microorganisms has historically been difficult because of interference by high background concentrations (780,840 ppm) of atmospheric N 2. Here, we applied a new automated technique for simultaneous measurement of the denitrification end‐products N 2 O and N 2 . We tested the hypothesis that the temperature response function (defined here as Q 10 ) for N 2 O was greater than for N 2 under anaerobic conditions in the laboratory. The Q 10 for N 2 O was 2.0 and the Q 10 for N 2 was 1.4, indicating differences in sensitivity to temperature. Denitrified‐N shifted towards N 2 O as temperature increased. While moisture strongly controls the relative abundance of denitrification end‐products, additional experiments are needed to determine how a wider range of temperatures may affect N 2 O and N 2 . Results could enhance understanding of temperature controls on N 2 O production and consumption processes.
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