H12C-05
Effects of Nitrogen Inputs and Watershed Characteristics on Summer Stream Nitrogen Concentrations: A National-Scale Analysis

Monday, 14 December 2015: 11:20
3020 (Moscone West)
Rebecca A Bellmore1, Jana Compton2, Marc Weber3, Ryan A Hill4, Darren Thornbrugh4 and J Renee Brooks2, (1)National Research Council, Ottawa, ON, Canada, (2)Environmental Protection Agency Corvallis, Western Ecology Division, Corvallis, OR, United States, (3)US EPA, Corvallis, OR, United States, (4)Oak Ridge Institute for Science and Education, Oak Ridge, TN, United States
Abstract:
Nitrogen (N) inputs to the landscape have been linked previously to N loads exported from watersheds at the national scale; however, stream N concentration is arguably more relevant than N load for drinking water quality, freshwater biological responses and establishment of nutrient criteria. In this study, we combine national-scale anthropogenic N input data, including synthetic fertilizer, crop biological N fixation, manure applied to farmland, atmospheric N deposition, and point source inputs, with data from the 2008-09 National Rivers and Streams Assessment to quantify the relationship between N inputs and in-stream concentrations of total N (TN), dissolved inorganic N (DIN), and total organic N (TON) (calculated as TN – DIN). In conjunction with simple linear regression, we use multiple regression to understand how watershed and stream reach attributes modify the effect of N inputs on N concentrations. Median TN was 0.50 mg N L-1 with a maximum of 25.8 mg N L-1. Total N inputs ranged from less than 1 to 196 kg N ha-1 y-1, with a median of 14.4 kg N ha-1 y-1. Atmospheric N deposition was the single largest anthropogenic N source in the majority of sites, but agricultural sources generally dominate total N inputs in sites with elevated N concentrations. The sum of all N inputs were positively correlated with concentrations of all forms of N [r2 = 0.44, 0.43, and 0.18 for TN, DIN, and TON, respectively (all log-transformed), n = 1112], indicating that watershed N inputs are strongly related to stream N concentrations during the summer, despite this being a biologically active and N-retentive period. Additionally, model results suggest that watershed characteristics like wetland area, riparian disturbance and forest cover moderate the effects of watershed N loading on in-stream N concentrations, and different forms of N are likely to respond differently to increasing agricultural and atmospheric N inputs depending on local watershed characteristics.