2012
DOI: 10.1029/2012jg001950
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Hydrologic connectivity increases denitrification in the hyporheic zone and restored floodplains of an agricultural stream

Abstract: [1] Stream ecotones, specifically the lateral floodplain and subsurface hyporheic zone, can be important sites for nitrogen (N) removal via denitrification, but their role in streams with constructed floodplains has not been examined. We studied denitrification in the hyporheic zone and floodplains of an agriculturally influenced headwater stream in Indiana, USA, that had floodplains added as part of a "two-stage ditch" restoration project. To examine the potential for N removal in the hyporheic zone, we seaso… Show more

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Cited by 83 publications
(76 citation statements)
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“…Thus, restored streams and floodplains may have high rates of N retention and removal because conditions can be favorable for both coupled nitrification-denitrification and assimilation [39][40][41]. As the mechanisms controlling N and P retention are different, the inclusion of macrophytes in stream and river restoration designs may be beneficial for retention of both N and P. This is because roots can oxygenate soil for coupled nitrification-denitrification and P immobilization [42,43].…”
Section: Stream Processes Driving Nutrient Cyclingmentioning
confidence: 99%
“…Thus, restored streams and floodplains may have high rates of N retention and removal because conditions can be favorable for both coupled nitrification-denitrification and assimilation [39][40][41]. As the mechanisms controlling N and P retention are different, the inclusion of macrophytes in stream and river restoration designs may be beneficial for retention of both N and P. This is because roots can oxygenate soil for coupled nitrification-denitrification and P immobilization [42,43].…”
Section: Stream Processes Driving Nutrient Cyclingmentioning
confidence: 99%
“…Floods could create ideal hydro-biogeochemical conditions for denitrification. For example, residence time in the riparian zone increases when the hydraulic head gradient between the aquifer and stream surface reverses injecting NO 3 -rich stream water into lowoxygen riparian groundwater rich in labile organic (Gu et al 2008(Gu et al , 2012Ocampo et al 2006;Roley et al 2012). Furthermore, loading of biogenic N 2 gas from groundwater to streams may increase during floods as rates of groundwater discharge increase.…”
Section: Controls Of N 2 and N 2 O Productionmentioning
confidence: 99%
“…Retaining vegetated benches increases the surface area of ditches and retention time during high flows. In Ohio and Indiana, denitrification rates have been found to be greater in sediments on naturally formed ditch benches than in sediments from side slopes of maintained trapezoidal ditches (Powell and Bouchard 2010), and having benches may influence in-stream denitrification rates (Roley et al 2012a(Roley et al , 2012b. Managing flow regimes in ditches can reduce N and moderate downstream P losses through greater capacity for sorption Strock et al 2007Strock et al , 2010Smith 2009).…”
Section: Figurementioning
confidence: 99%
“…A simulation study found that if 1% of a watershed was converted to benches within ditches, the increased storage could remove up to 20% of NO 3 -N loading in the system (Kallio 2010). There is extensive research on quantifying N removal rates and sediment dynamics in several ditches in Indiana, Michigan, and Ohio (Roley et al 2012a(Roley et al , 2012bRoley et al 2014;Davis et al 2015). At a constructed two-stage ditch in the Tippecanoe River watershed in Indiana, monitoring began one year prior to two-stage construction in both an upstream control and a downstream treatment reach and has continued for several years postconstruction.…”
Section: Figurementioning
confidence: 99%