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Occurrence of Nitrate in Groundwater—A Review
Author(s) -
Spalding R. F.,
Exner M. E.
Publication year - 1993
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/jeq1993.00472425002200030002x
Subject(s) - aquifer , groundwater , environmental remediation , environmental science , hydrology (agriculture) , drainage , hydrogeology , irrigation , tile drainage , nitrate , water well , surficial aquifer , manure , soil water , contamination , geology , groundwater recharge , soil science , ecology , geotechnical engineering , biology
The results of federal, state, and local surveys, which included more than 200 000 NO 3 ‐N data points, are summarized in this review of NO 3 in groundwater in the USA. The levels of NO 3 ‐N are associated with source availability and regional environmental factors. In regions where well‐drained soils are dominated by irrigated cropland, there is a strong propensity toward the development of large areas with groundwater that exceeds the maximum contaminant level of 10 mg/L NO 3 ‐N. Most of these areas are west of the Missouri River where irrigation is a necessity. Aquifers in highly agricultural areas in the southeastern USA reportedly are not contaminated. Vegetative uptake and denitrification in this warm, wet, C‐rich environment are responsible for the natural remediation of NO 3 in shallow aquifers. In the Middle Atlantic states and the Delmarva Peninsula, localized contamination occurs beneath cropped, well‐drained soils that receive excessive applications of manure and commercial fertilizer. Extensive tile drainage has for the most part prevented a NO 3 problem in the groundwater of the Corn Belt states. Throughout the USA there are recurring themes. They include a decrease in NO 3 ‐N levels with depth; lower NO 3 ‐N levels in shallow wells (< 8 m); and a significant increase in NO 3 ‐N in older wells and in wells with poor construction. The factors affecting the distribution of NO 3 in aquifers are complex and poorly understood. Interdisciplinary studies using discrete depth sampling, hydrogeological indicators, isotopic tracers, and microbiological techniques are necessary to unravel the complex dynamics.