4.7 Article

Denitrification and dilution along fracture flowpaths influence the recovery of a bedrock aquifer from nitrate contamination

Journal

SCIENCE OF THE TOTAL ENVIRONMENT
Volume 569, Issue -, Pages 450-468

Publisher

ELSEVIER
DOI: 10.1016/j.scitotenv.2016.06.091

Keywords

Point-source; Non-point source; Monitoring; Planar structures; Anisotropy; Nutrient management

Funding

  1. Environmental Protection Agency - Section 319 program [98160602]
  2. U.S. Geological Survey STATEMAP program [02HQAG0049]

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In 2000, elevated nitrate concentrations ranging from 12 to 34 mg/LNO3-N were discovered in groundwater from numerous domestic bedrock wells adjacent to a large dairy farm in central Vermont. Long-term plots and contours of nitrate vs. time for bedrock wells showed little/no, moderate, and large change patterns that were spatially separable. The metasedimentary bedrock aquifer is strongly anisotropic and groundwater flow is controlled by fractures, bedding/foliation, and basins and ridges in the bedrock surface. Integration of the nitrate concentration vs. time data and the physical and chemical aquifer characterization suggest two nitrate sources: a point source emanating from a waste ravine and a non-point source that encompasses the surrounding fields. Once removed, the point source of NO3 ( manure deposited in a ravine) was exhausted and NO3 dropped from 34 mg/L to <10 mg/L after similar to 10 years; however, persistence of NO3 in the 3 to 8 mg/L range (background) reflects the long term flux of nitrates from nutrients applied to the farm fields surrounding the ravine over the years predating and including this study. Inferred groundwater flow rates from the waste ravine to either moderate change wells in basin 2 or to the shallow bedrock zone beneath the large change wells are 0.05 m/day, well within published bedrock aquifer flow rates. Enrichment of N-15 and O-18 in nitrate is consistent with lithotrophic denitrification of NO3 in the presence of dissolved Mn and Fe. Once the ravine point-source was removed, denitrification and dilution collectively were responsible for the down-gradient decrease of nitrate in this bedrock aquifer. Denitrification was most influential when NO3-N was >10 mg/L. Our multidisciplinary methods of aquifer characterization are applicable to groundwater contamination in any complexly-deformed and metamorphosed bedrock aquifer. (C) 2016 Elsevier B.V. All rights reserved.

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