Global Change Biology · 2018 · 59 citations · 55 references
AgricultureEnvironmental SciencesSoil SciencesSoil BiogeochemistrySoil MicrobiologySoil ScienceNitrogen CycleNitrogen CyclingNitrogen FixationNitrogen OxidesSoil Nitrogen ChemistrySoil Nutrient CyclingGaseous EmissionsMicrobial Nitrogen CyclingMicrobial Nitrogen TransformationsMicrobial Nitrogen TurnoverNitrogen Cycling DynamicsSoil Greenhouse Gas EmissionsSoil Nitrogen DynamicsSoil Nitrogen Temporal Dynamics
Abstract Rising atmospheric CO 2 concentrations are expected to increase nitrous oxide (N 2 O) emissions from soils via changes in microbial nitrogen (N) transformations. Several studies have shown that N 2 O emission increases under elevated atmospheric CO 2 ( eCO 2 ), but the underlying processes are not yet fully understood. Here, we present results showing changes in soil N transformation dynamics from the Giessen Free Air CO 2 Enrichment (Gi FACE ): a permanent grassland that has been exposed to eCO 2 , +20% relative to ambient concentrations ( aCO 2 ), for 15 years. We applied in the field an ammonium‐nitrate fertilizer solution, in which either ammonium ( ) or nitrate ( ) was labelled with 15 N. The simultaneous gross N transformation rates were analysed with a 15 N tracing model and a solver method. The results confirmed that after 15 years of eCO 2 the N 2 O emissions under eCO 2 were still more than twofold higher than under aCO 2 . The tracing model results indicated that plant uptake of did not differ between treatments, but uptake of was significantly reduced under eCO 2 . However, the and availability increased slightly under eCO 2 . The N 2 O isotopic signature indicated that under eCO 2 the sources of the additional emissions, 8,407 μg N 2 O–N/m 2 during the first 58 days after labelling, were associated with reduction (+2.0%), oxidation (+11.1%) and organic N oxidation (+86.9%). We presume that increased plant growth and root exudation under eCO 2 provided an additional source of bioavailable supply of energy that triggered as a priming effect the stimulation of microbial soil organic matter ( SOM ) mineralization and fostered the activity of the bacterial nitrite reductase. The resulting increase in incomplete denitrification and therefore an increased N 2 O:N 2 emission ratio, explains the doubling of N 2 O emissions. If this occurs over a wide area of grasslands in the future, this positive feedback reaction may significantly accelerate climate change.
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