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<br />water to the river. In general, mass balance and <br />instantaneous measurements of ground-water <br />discharge indicated that the ground-water flow <br />system in the vicinity of the river consisted of a <br />large-area flow system that provided a net addition <br />of water to the river and a small-area flow system <br />that cycled water in and out of the riverbed sedi- <br />ments, but provided no net addition of water to the <br />river. The small.area flow system was superim- <br />posed on the large-area flow system. <br /> <br />The median values of pH and dissolved <br />oxygen in ground water from the large-area flow <br />system were 7.16 and 0.9 milligrams per liter. <br />These values were lower than values for river <br />water, indicating that the discharge of ground <br />water from the large-area flow system would <br />lower values of pH and concentrations of dis- <br />solved oxygen in the river. Concentrations of <br />dissolved nitrite plus nitrate, ammonium, and <br />phosphorus in ground water from the large-area <br />flow system varied between monitoring-well sites. <br />The highest concentrations of nitrite plus nitrate <br />(maximum concentration of37,93 milligrams per <br />liter as nitrogen) were measured in water from <br />wells along the downstream river reach where rel- <br />atively low concentrations of dissolved oxygen <br />occurred in the river. The highest concentrations <br />of ammonium and phosphorus (maximum concen- <br />trations of9.2 milligrams per liter as nitrogen and <br />7.24 milligrams per liter as phosphorus) were <br />measured in water from wells along the upstream <br />river reach where relatively low concentrations of <br />dissolved oxygen occUlTed in the river. The water- <br />quality data indicate that ground-water discharge <br />from the large-area flow system may have been a <br />source of nitrite plus nitrate to the downstream <br />liver reach and a source of ammonium and phos- <br />phorus to the upstream river reach. <br /> <br />The median values of pH and dissolved <br />oxygen in ground water from the small-area flow <br />system were 7.33 and 0.2 milligrams per liter. The <br />dissolved-oxygen data indicate that sediments in <br />the small-area flow system were a sink for dis- <br />solved oxygen in water discharging to the river <br />from the large-area flow system and in surface <br />water infiltrating into the bed sediments. These <br />data indicate that even though the small-area flow <br />system was not a net source of water to the river, it <br />did have the potential to lower concentrations of <br />dissolved oxygen in the river as river water cycled <br /> <br />in and out of the bed sediments. Chemical and iso- <br />topic data indicate that organic-rich bed sediments <br />in the upstream river reach were a source of <br />ammonium and phosphorus to water in the small- <br />area flow system; therefore, the small.area flow <br />system may have been a source of ammonium <br />and phosphorus to the river even though it was <br />not a net source of water to the river. Laboratory <br />measurements of denitrification in bed sediments <br />from below the river indicate that sediments in the <br />small-area flow system also were a potential sink <br />for nitrate in the large-area flow system and in the <br />river as a result of microbial denitrification in the <br />sediments. The widespread distribution of sources <br />and sinks of dissolved-nitrogen and -phosphorus <br />species made it difficult to detennine how much <br />nitrogen and phosphorus were entering the river <br />from ground-water discharge. <br /> <br />INTRODUCTION <br /> <br />The South Platte River between Denver and <br />Fort Lupton has been designated by the Colorado <br />Department of Health and Environment, Water Quality <br />Control Commission (WQCC), as an Aquatic Life <br />Wann Water Class 2 river (Colorado Department of <br />Health and Environment, 1993). As such, the WQCC <br />has set minimum 24-hour average dissolved-oxygen <br />(DO) concentrations of 5.0 mg/L from May through <br />July and 4.5 mg/L from August through April to sus- <br />tain aquatic life in the river. Water-quality studies con- <br />ducted by the Metro Wastewater Reclamation District <br />(MWRD) have indicated that segments ofthis reach <br />do not meet the DO standards during some periods of <br />low flow. Although effluent discharged from the <br />MWRD central plant has been identified as an impor- <br />tant contributing factor in the DO depletion (Camp <br />Dresser and McKee, Inc., 1992), other unrelated pro- <br />cesses also may affect DO concentrations in the river <br />during low flow. Other sources of water to the river <br />include ungaged surface runoff, tributary inflows, and <br />ground-water discharge. Previous work conducted by <br />the U.S. Geological Survey (USGS) indicates that <br />ground-water discharge to this reach ofthe South Platte <br />River is a substantial source of water to the river when <br />runoff and tributary inflows are at a minimum (Hurr <br />and Schneider, 1972) and that biological reactions <br />in riverbed sediments at the interface between surface <br />water and ground water are an important sink for <br />DO in ground-water discharge (P.B. McMahon, <br />U.S. Geological Survey, unpublished data, 1993). <br />Discharge of DO-depleted ground water may contrib- <br />ute to the low DO concentrations in the South Platte <br /> <br />2 Quantlly and Quallly of Ground.Watar Dlacharga to tha South Platta River, Danvar to Fort Lupton, Colorado, <br />Auguat 1992 Through July 1993 <br />