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Mechanistic Modeling of Nitrite Accumulation and Nitrogen Oxide Gas Emissions during Nitrification
Author(s) -
Venterea R. T.,
Rolston D. E.
Publication year - 2000
Publication title -
journal of environmental quality
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.888
H-Index - 171
eISSN - 1537-2537
pISSN - 0047-2425
DOI - 10.2134/jeq2000.00472425002900060003x
Subject(s) - nitrification , nitrous oxide , nitrobacter , environmental chemistry , nitrite , chemistry , nitrogen , fertilizer , trace gas , environmental engineering , environmental science , nitrate , organic chemistry
Nitrite (NO − 2 ) accumulation in soil following nitrogen (N) fertilizer application has been observed under a variety of conditions. The presence of NO − 2 together with soil acidity results in the formation of nitrous acid (HNO 2 ), which decomposes abiotically to produce nitric oxide (NO) and nitrous oxide (N 2 O). These N oxide trace gases have potential effects on several atmospheric processes. Presented here is a model that describes some of the interactions between microbial, chemical, and physical processes that influence NO − 2 accumulation and N oxide gas emissions following applications of NH + 4 ‐based fertilizers. The model is applied to hypothetical and actual field scenarios. A two‐step, two‐population nitrification submodel is linked to gas production and transformation submodels. Transport of all chemical species occurs by diffusion. The model results suggest that some degree of transient nitrite accumulation following NH + 4 application is a consequence of the nature of nitrification itself. Model simulations and sensitivity analysis indicate that (i) soils receiving similar fertilizer treatments but differing in their ability to buffer nitrification‐induced acidity may produce dramatically different N oxide gas emissions, (ii) subsurface fertilizer placement can significantly reduce net NO emissions, and (iii) the differential responses of Nitrosomonas and Nitrobacter populations to chemical toxicities associated with the form and/or rate of fertilizer application may significantly affect the extent of NO − 2 accumulation and corresponding gas emissions. Overall, the results contribute to our basic understanding of how multiple microbial, chemical, and physical factors can interact to control the net soil‐to‐atmosphere emission of nitrification‐derived NO and N 2 O.