Glenn S. Warner
University of Connecticut
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Lake and Reservoir Management | 2007
Farhad Nadim; Amvrossios C. Bagtzoglou; George E. Hoag; Fred L. Ogden; Glenn S. Warner; David M. Soballe
Abstract Mansfield Hollow Lake (MHL) and Willimantic Reservoir (WR) are two reservoir lakes located in eastern Connecticut in the northeastern United States. MHL formed behind the Mansfield Hollow Dam constructed by the U.S. Army Corps of Engineers in 1952 and is primarily fed by the Fenton, Mount Hope and Natchaug Rivers. The WR lies approximately 1-km downstream from the Mansfield Hollow Dam. Total dissolved nitrogen, phosphorus and chlorophyll a measurements indicate the water bodies could be classified as borderline mesotrophic/eutrophic. A steady-state numerical software package (Bathtub) designed to facilitate application of empirical eutrophication models to morphometrically complex reservoirs was used to determine the trophic status in MHL and WR based on different phosphorus and nitrogen loading budgets. The short hydraulic residence times and rapid flushing rates in MHL and WR are directly related to the flow rates in the streams discharging into MHL. The low flow period could significantly increase the hydraulic residence times of these two reservoirs. Therefore, the sampling design emphasized periods of low flow in late August and early September to assess the impact of nutrient inputs to MHL and WR during dry periods. The results of a low flow sampling period (August 2002) were used to calibrate and test the Bathtub model developed for these water bodies. Application of the Bathtub model to differing flow regimes, notably average flows, suggested that nitrogen or phosphorus could limit the productivity and cause eutrophication in the two lakes. Results of this study indicated that the Bathtub model could be used to predict total nitrogen and total phosphorus concentrations with reasonable accuracy, but it might not be a suitable tool for predicting organic nitrogen or algae in rapidly flushing lake systems. To further investigate and validate the assumptions made in this study, more sampling data are needed, especially during high intensity storm events to investigate possible sources of nutrient flow into the two lake system and further calibrate the Bathtub model for the MHL-WR watershed.
Journal of The American Water Resources Association | 2007
Mark Hood; John C. Clausen; Glenn S. Warner
Journal of The American Water Resources Association | 2003
Déborah M. Santos‐Román; Glenn S. Warner; Frederick N. Scatena
Journal of The American Water Resources Association | 2002
Hector D. Rivera-Ramirez; Glenn S. Warner; Frederick N. Scatena
Archive | 2002
David R Miller; Glenn S. Warner; Fred L. Ogden; Arthur T DeGaetano
Journal of The American Water Resources Association | 1996
Andres R. Garcia-Martino; Frederick N. Scatena; Glenn S. Warner; Daniel L. Civco
Archive | 2006
Glenn S. Warner; Fred L. Ogden; Amvrossios C. Bagtzoglou; Piotr Parasiewicz
Journal of Environmental Management | 2016
Janet R. Barclay; Hannah Tripp; Christopher J. Bellucci; Glenn S. Warner; Ashley M. Helton
Water Environment Research | 2007
Farhad Nadim; Amvrossios C. Bagtzoglou; Sandrine A. Baun; Glenn S. Warner; Fred L. Ogden; Richard A. Jacobson; Piotr Parasiewicz
International Journal of Ecological Economics and Statistics | 2008
Richard A. Jacobson; Glenn S. Warner; Piotr Parasiewicz; Amvrossios C. Bagtzoglou; Fred L. Ogden