A better understanding of the internal N cycle in agriculturally used soils is crucial for developing sustainable and environmentally friendly N fertilizer management and to propose effective N 2 O mitigation strategies. The present laboratory study quantifies gross nitrogen transformations in an intensively used agricultural soil of the North China Plain (NCP). It also elucidates the role of nitrification and denitrification in the emissions of the greenhouse gas N 2 O. In the lab, soil samples adjusted to a water‐filled pore space (WFPS) of 40 or 60% were spiked with 15 NH 4 NO 3 , NH 4 15 NO 3 , or 15 NH 4 15 NO 3 and incubated at 20°C for 10 d. One subset of the samples was amended with glucose. The size and 15 N enrichment of the mineral N pools and N 2 O fluxes were determined at intervals of 0 to 10 d. The studied calcareous soil showed a very rapid nitrification of the applied NH 4 + , which disappeared during the first 3 d. Glucose enhanced mineralization of native soil organic matter (SOM), stimulated dissimilatory nitrate reduction to ammonium (DNRA), and promoted the immobilization–remineralization cycle. Throughout the incubation, nitrification, and denitrification occurred simultaneously. Nitrification was the dominant N 2 O‐producing process and contributed 83.0 to 95.4% to the totally emitted N 2 O in the non‐glucose soils. In contrast, the N 2 O emitted from 15 NO 3 − pool increased after adding glucose, indicating that denitrification was C‐limited in the studied soil.
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Wan et al. (2009) studied this question.
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