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Denitrification Enzyme Activity as an Indicator of Nitrate Movement through a Diversion Wetland
Author(s) -
Gardner Lisa M.,
White John R.
Publication year - 2010
Publication title -
soil science society of america journal
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.836
H-Index - 168
eISSN - 1435-0661
pISSN - 0361-5995
DOI - 10.2136/sssaj2008.0354
Subject(s) - denitrification , wetland , soil water , environmental science , marsh , hydrology (agriculture) , nitrate , nitrogen , ecology , soil science , geology , chemistry , biology , geotechnical engineering , organic chemistry
The Davis Pond freshwater diversion is intended to help restore Louisiana's coastal wetlands by reintroducing Mississippi River water to Barataria Basin. We hypothesized that the high NO 3 − concentration (2.0 mg NO 3 –N L −1 ) of the Mississippi River water would control the rate of denitrification in the receiving marsh given that the soils are saturated, anaerobic, and contain high C. Therefore, areas of high denitrification enzyme activity (DEA) in the marsh would represent soils exposed to river NO 3 − and actively involved in denitrification. Data from 88 soil samples (0–10 cm) collected throughout the marsh revealed significantly higher rates of DEA in a 715‐ha area adjacent to the diversion inflow. This area of generally high DEA contained >80% of all DEA observed while representing only 19% of the total marsh area at the low discharge rate of 39.5 m 3 s −1 The area of high DEA coincided with the highest surface water NO 3 − and indicated that the marsh has a greater aerial capacity for NO 3 − removal than is utilized. A laboratory experiment suggested that soils loaded with external NO 3 − typically had higher DEA rates than soils receiving no added NO 3 − The DEA was strongly dependent on soil depth (92% of DEA occurred at 0–5 cm) and internal N cycling was substantial in this wetland soils. This study demonstrates the applicability of using soil DEA to map where denitrification activity is greatest, the aerial extent of soils involved in denitrification, and the general flow path of introduced nutrients in large wetlands where NO 3 − is the limiting factor for denitrification.