4.7 Article

A global synthesis of soil denitrification: Driving factors and mitigation strategies

Journal

AGRICULTURE ECOSYSTEMS & ENVIRONMENT
Volume 327, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.agee.2021.107850

Keywords

Denitrification; N2O/(N2O+N-2) ratio ; Global synthesis; Meta-analysis; Mitigation strategies

Funding

  1. Australian Research Council Linkage Project [LP160101417]
  2. Australian Research Council (ARC) Research Hub for Innovative Nitrogen Fertilizers and Inhibitors [IH200100023]
  3. Australian Government Research Training Program Scholarship
  4. Australian Research Council [LP160101417, IH200100023] Funding Source: Australian Research Council

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Soil denitrification can lead to significant nitrogen loss, and the denitrification rate is positively correlated with soil water content, nitrate content, and temperature, with an average emission factor of 4.8% and an average N2O/(N2O+N-2) ratio of 0.33. Latitude, water content, soil mineral nitrogen, and soil oxygen content affect N-2 emissions, while soil oxygen content, organic carbon, C/N ratio, soil pH, and water content affect the N2O/(N2O+N-2) ratio. Optimizing nitrogen application, using ammonium-based fertilizers, applying biochar, and using nitrification inhibitors can effectively reduce soil denitrification rate and N-2 emissions.
Dinitrogen (N-2) and nitrous oxide (N2O) produced via denitrification may represent major nitrogen (N) loss in terrestrial ecosystems. A global assessment of soil denitrification rate, N2O/(N2O+N-2) ratio, and their driving factors and mitigation strategies is lacking. We conducted a global synthesis using 225 studies (3367 observations) to fill this knowledge gap. We found that daily N loss through soil denitrification varied with ecosystems and averaged 0.25 kg N ha(-1). The average emission factor of denitrification (EFD) was 4.8%. The average N2O/ (N2O+N-2) ratio from soil denitrification was 0.33. Soil denitrification rate was positively related to soil water filled pore space (WFPS) (p < 0.01), nitrate (NO3-) content (p < 0.05) and soil temperature (p < 0.01), and decreased with higher soil oxygen content (p < 0.01). N-2 emissions increased with latitude (p < 0.05), WFPS (p < 0.01) and soil mineral N (p < 0.05) but decreased with soil oxygen content (p < 0.05). The N2O/(N2O+N-2) ratio increased with soil oxygen content (p < 0.01) but decreased with organic carbon (C) (p < 0.05), C/N ratio (p < 0.01), soil pH (p < 0.05) and WFPS (p < 0.01). We also found that optimizing N application rates, using ammonium-based fertilizers compared to nitrate-based fertilizers, biochar amendment, and application of nitrification inhibitors could effectively reduce soil denitrification rate and associated N-2 emissions. These findings highlight that N loss via soil denitrification and N-2 emissions cannot be neglected, and that mitigation strategies should be adopted to reduce N loss and improve N use efficiency. Our study presents a comprehensive data synthesis for large-scale estimations of denitrification and the refinement of relevant parameters used in the submodels of denitrification in process-based models.

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