Unearthing a stream-wetland floodplain system: increased denitrification and nitrate retention at a legacy sediment
Kenneth J Forshay1, Julie N Weitzman2, Jessica F Wilhelm3
1Groundwater Characterization and Remediation Division, Center for Environmental Solutions and Emergency Response, Office of Research and Development, Environmental Protection Agency, Ada, OK, USA.
Abstract:
Nitrogen (N) retention is a common goal of stream-wetland restoration projects in systems with excess nitrate ( ), however N retention depends on habitats with high denitrification and uptake rates that interact with . Legacy sediments deposited along formerly impounded streams bury and disconnect historic floodplain-wetland systems. This disconnection limits sediment-water interactions, decreases N retention and increases N delivery. Restoration with legacy sediment removal should lead to greater N retention due to the reestablishment of wet habitats that interact with -rich water, but the formation of biogeochemically retentive soils under modern conditions of high , N retention rates, and recovery time are unclear. An experimental restoration approach undertaken at Big Spring Run in Lancaster, PA, USA was used to test the hypothesis that reconnection of a stream to its historic floodplain with legacy sediment removal enhances N processing and retention. We describe changes in sediment and water concentrations of N and organic carbon (C) along with the changes in sediment biogeochemical processing rates of denitrification, nitrification, and C mineralization, before and for five years following restoration. Our results show that biogeochemical processing increased and higher retention developed following stream-wetland restoration. retention improved after several years as organic matter accumulated to ultimately support higher rates of denitrification that transitioned from organic C limitation to limitation. We conclude that, in systems with high contemporary , restoration via legacy sediment removal and floodplain reconnection can lead to the accumulation of organic matter and improved biogeochemical retention over time.
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