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Soil Denitrification and Nitrous Oxide Losses under Corn Irrigated with High‐Nitrate Groundwater
Author(s) -
Qian Jin H.,
Doran John W.,
Weier Keith L.,
Mosier Arvin R.,
Peterson Todd A.,
Power James F.
Publication year - 1997
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/jeq1997.00472425002600020004x
Subject(s) - denitrification , nitrous oxide , leaching (pedology) , environmental science , irrigation , groundwater , nitrate , soil water , growing season , fertilizer , agronomy , water quality , surface water , nitrogen , hydrology (agriculture) , environmental chemistry , environmental engineering , chemistry , soil science , ecology , biology , geotechnical engineering , organic chemistry , engineering
Inappropriate management of irrigation water and fertilizer N in irrigated corn ( Zea mays L.) has resulted in excess N leaching from the rooting zone and NO − 3 contamination of groundwater. A better understanding of microbially mediated conversion of plant available N to gaseous N forms is needed for more efficient N use, to evaluate the impact of radiatively important gas production such as nitrous oxide (N 2 O) on air quality, and to determine the potential of microbial denitrification for remediating high‐NO − 3 irrigation water. Soil denitrification and N 2 O losses from pivot irrigated corn were measured during the 1991 and 1992 growing seasons using surface gas chambers at the Management System Evaluation Area (MSEA) site for water quality research in the Central Platte Valley near Shelton, NE. Denitrification and N 2 O losses remained low throughout most of the growing season, generally ranging from 10 to 50 g N ha −1 d −1 , when soil water contents were generally below 60% water‐filled pore space (WFPS). Nitrous oxide was the major gaseous N product under these conditions. When soils were wetted by irrigation or rainfall to >70% WFPS, denitrification losses ranged from 0.2 to 1.4 kg N ha −1 d −1 with N 2 comprising 80 to 98% of the denitrification gases measured. Monthly average denitrification losses across years were highly correlated ( r = 0.693) with time of growing season, suggesting a possible link between plant growth and denitrification. Seasonal gaseous N losses via denitrification and N 2 O emission from irrigated corn represented 1 to 5% of the N applied as fertilizer or in irrigation water during a relatively dry 1991 season and the 1992 season with near normal precipitation. Results of our 2‐yr study indicate that under good irrigation and N management practices gaseous N losses from denitrification and N 2 O production pose little additional threat to atmospheric quality or N‐use efficiency but also provide little hope for bioremediation of high‐NO − 3 groundwater.