North-Central Section - 47th Annual Meeting (2-3 May 2013)

Paper No. 7
Presentation Time: 10:20 AM

GREENHOUSE GAS EMISSIONS FROM A TEMPERATE AGRICULTURAL RESERVOIR


SMOLENSKI, Rebecca Lynn, Geological Sciences, University of Cincinnati, 3352 jefferson ave, apt 2, Cincinnati, OH 45220, BEAULIEU, Jake, Environmental Protection Agency, Cincinnati, OH 45268 and TOWNSEND-SMALL, Amy, Department of Geology and Department of Geography, University of Cincinnati, 605 Geology-Physics Building, Cincinnati, OH 45221, smolenrl@gmail.com

Reservoirs are being built at an increasing rate each year to provide humans with resources such as hydroelectric power and drinking water. These man made systems have provided society with important services but these have come at the cost of enhanced greenhouse gas (GHG) emissions. Recent estimates suggest reservoirs are a globally significant source of GHG emissions but these estimates are largely based on studies of oligotrophic boreal and tropical reservoirs. Reservoirs draining agricultural basins are common throughout much of the developed and are subject to high nutrient loading rates from the watershed. Excess nutrient loading stimulates algae blooms and degrades water quality in these reservoirs but surprisingly little is known about how nutrients and algal blooms affect GHG dynamics. To assess GHG dynamics in an agricultural reservoir we measured GHG emission rates, dissolved concentrations and nutrient chemistry in William H. Harsha Lake, an agricultural reservoir located in southwestern Ohio on a monthly basis since October 2011.

Average daily emissions of methane (CH4) were 50 mg CH4-C m-2 d-1 . The highest emissions rates of CH4 were observed during the summer months and during fall turnover, and the lowest emissions were observed during the winter. Depth profiles of dissolved CH4 throughout the summer show an accumulation of CH4 in the hypolimnium while the lake is thermally stratified.

Average daily nitrous oxide (N2O) emissions were 0.80 mg N2O-N m-2 d-1 . The highest emissions were during fall turnover. During late summer, parts of the lake became a sink for N2O, and depth profiles of N2O show a similar trend with the water column becoming undersaturated with N2O during this time. Without N2O accumulation in the water column during thermal stratification, it is likely that the source of N2O during fall turnover is nitrification of remineralized ammonium.