TY - JOUR
T1 - Quantifying the fate of agricultural nitrogen in an unconfined aquifer
T2 - Stream-based observations at three measurement scales
AU - Gilmore, Troy E.
AU - Genereux, David P.
AU - Solomon, D. Kip
AU - Solder, John E.
AU - Kimball, Briant A.
AU - Mitasova, Helena
AU - Birgand, François
N1 - Funding Information:
Data used for tables and figures are available from the corresponding author upon request. This project was funded by National Science Foundation under Awards EAR- 1045162 to North Carolina State University and EAR-1045134 to the University of Utah. The authors gratefully acknowledge assistance with field work: Matt Burnette and Scott Becker (both NC State) in July 2012 and March 2013, and Kyle Aveni- Deforge (NC State), Casey Kennedy (USDA-ARS), Matt Webb (Arcadis U.S.), and Vic Heilweil and James Marlowe (USGS) in March 2013.
Publisher Copyright:
© 2016. American Geophysical Union. All Rights Reserved.
PY - 2016/3/1
Y1 - 2016/3/1
N2 - We compared three stream-based sampling methods to study the fate of nitrate in groundwater in a coastal plain watershed: point measurements beneath the streambed, seepage blankets (novel seepage-meter design), and reach mass-balance. The methods gave similar mean groundwater seepage rates into the stream (0.3-0.6 m/d) during two 3-4 day field campaigns despite an order of magnitude difference in stream discharge between the campaigns. At low flow, estimates of flow-weighted mean nitrate concentrations in groundwater discharge ([ NO3-]FWM) and nitrate flux from groundwater to the stream decreased with increasing degree of channel influence and measurement scale, i.e., [ NO3-]FWM was 654, 561, and 451 μM for point, blanket, and reach mass-balance sampling, respectively. At high flow the trend was reversed, likely because reach mass-balance captured inputs from shallow transient high-nitrate flow paths while point and blanket measurements did not. Point sampling may be better suited to estimating aquifer discharge of nitrate, while reach mass-balance reflects full nitrate inputs into the channel (which at high flow may be more than aquifer discharge due to transient flow paths, and at low flow may be less than aquifer discharge due to channel-based nitrate removal). Modeling dissolved N2 from streambed samples suggested (1) about half of groundwater nitrate was denitrified prior to discharge from the aquifer, and (2) both extent of denitrification and initial nitrate concentration in groundwater (700-1300 μM) were related to land use, suggesting these forms of streambed sampling for groundwater can reveal watershed spatial relations relevant to nitrate contamination and fate in the aquifer.
AB - We compared three stream-based sampling methods to study the fate of nitrate in groundwater in a coastal plain watershed: point measurements beneath the streambed, seepage blankets (novel seepage-meter design), and reach mass-balance. The methods gave similar mean groundwater seepage rates into the stream (0.3-0.6 m/d) during two 3-4 day field campaigns despite an order of magnitude difference in stream discharge between the campaigns. At low flow, estimates of flow-weighted mean nitrate concentrations in groundwater discharge ([ NO3-]FWM) and nitrate flux from groundwater to the stream decreased with increasing degree of channel influence and measurement scale, i.e., [ NO3-]FWM was 654, 561, and 451 μM for point, blanket, and reach mass-balance sampling, respectively. At high flow the trend was reversed, likely because reach mass-balance captured inputs from shallow transient high-nitrate flow paths while point and blanket measurements did not. Point sampling may be better suited to estimating aquifer discharge of nitrate, while reach mass-balance reflects full nitrate inputs into the channel (which at high flow may be more than aquifer discharge due to transient flow paths, and at low flow may be less than aquifer discharge due to channel-based nitrate removal). Modeling dissolved N2 from streambed samples suggested (1) about half of groundwater nitrate was denitrified prior to discharge from the aquifer, and (2) both extent of denitrification and initial nitrate concentration in groundwater (700-1300 μM) were related to land use, suggesting these forms of streambed sampling for groundwater can reveal watershed spatial relations relevant to nitrate contamination and fate in the aquifer.
KW - coastal plain
KW - denitrification
KW - groundwater contamination
KW - hyphoreic zone
KW - nonpoint source nitrogen
KW - unconfined aquifer
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U2 - 10.1002/2015WR017599
DO - 10.1002/2015WR017599
M3 - Article
AN - SCOPUS:84977952435
VL - 52
SP - 1961
EP - 1983
JO - Water Resources Research
JF - Water Resources Research
SN - 0043-1397
IS - 3
ER -