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Linking Soil Erosion to Instream Dissolved Phosphorus Cycling and Periphyton Growth
Authors:RB Brennan  JT Scott  AN Sharpley  HT Lally  HP Jarvie  MJ Bowes  BE Haggard  E Gbur
Institution:1. Civil Engineering, National University of Ireland Galway, Galway, Ireland;2. Department of Biology, Baylor University, Waco, Texas;3. Department of Crop, Soil, and Environmental Sciences, University of Arkansas, Fayetteville, Arkansas;4. Freshwater Ecology, Galway‐Mayo Institute of Technology, Galway, Ireland;5. Centre for Ecology and Hydrology, Wallingford, United Kingdom;6. Department of Biological and Agricultural Engineering Systems, University of Arkansas, Fayetteville, Arkansas;7. Agricultural Statistics Laboratory, University of Arkansas, Fayetteville, Arkansas
Abstract:Phosphorus (P) is a limiting nutrient in freshwater systems and when present in runoff from agricultural lands or urban centers may contribute to excessive periphyton growth. In this study, we examined the link between soil erosion and delivery of eroded soil to streams during flow events, and the impact of that freshly deposited soil on dissolved reactive P (DRP) concentrations and periphyton growth under baseflow conditions when the risk of stream eutrophication is greatest. A microcosm experiment was designed to simulate the release of P from soil which had been amended with different amounts of P fertilizer to overlying water during baseflow conditions. Unglazed tiles, inoculated for five days in a second order stream, were incubated for seven days in microcosms containing soil with eight levels of soil Mehlich‐3 plant available phosphorus (M3P) ranging from 20 to 679 mg/kg M3P. Microcosm DRP was monitored. Following incubation tiles were scraped and the periphyton analyzed for chlorophyll a. Microcosm DRP concentrations increased with increasing soil M3P and equilibrium phosphorus concentration (EPC0). Relationships between M3P, EPC0, and DRP were nonlinear and increases in soil M3P and/or DRP had a greater impact on biomass accumulation when these parameters were above threshold values of 30 mg/kg M3P and 0.125 mg/L DRP. Significantly, this ecological threshold corresponds to the agronomic thresholds above which increased soil M3P does not increase plant response.
Keywords:fluvial‐sediment  phosphorus  ecology  freshwater  agriculture  diffuse pollution  chlorophyll a
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