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<br />depth. Ifwater depth was greater than 2.5 ft, velocity <br />was measured at a depth of 0.2 times the total depth and <br />at a depth of 0.8 times the total depth, and the velocities <br />were averaged. Velocity was multiplied by the area of <br />the incrementto determine volumetric discharge (cubic <br />feet per second) for each increment. Incremental dis- <br />charges were summed to detennine total surface-water <br />discharge. Accuracy of the discharge measurements <br />was about:1:5 percent. <br /> <br />Ground-water discharge to the South Platte <br />River was measured using indirect and direct tech- <br />niques, Indirect measurements of ground-water <br />discharge were obtained by calculating a mass balance <br />of all measured surface-water inflows and outflows to <br />three reaches of the river and by attributing the differ- <br />ence between inflows and outflows to ground-water <br />discharge. This indirect measurement of ground-water <br />discharge is called the incremental ground-water <br />discharge in the following discussion. The three <br />reaches of the South Platte River used in the mass <br />balance extend from 64th Avenue to 88th Avenue, <br />104th Avenue to upstream from the Brighton Ditch <br />headgate, and 160th Avenue to Highway 52 (pI. I). <br />Measurement~ of surface-water discharge were <br />made at the sites listed in table I. In addition, the <br />reaches were floated by boat to locate intennittent <br />flows not identified on maps. These flows usually were <br />from gravel-mine dewatering operations or were <br />ungaged irrigation return flows. These measurements <br />did not take into account surface-water losses from <br />evapotranspiration, which is an unknown quantity for <br />this study area. Indirect measurements of ground- <br />water discharge were made from August 1992 through <br />January 1993 and in May and July 1993. <br /> <br />River stage needs to be constant, or fluctu- <br />ations in stage need to be accounted for, to use the <br />ma.~s-balance technique for estimating ground-water <br />discharge. To minimize change in storage in the river, <br />discharge measurements made on the South Platte <br />River were timed using time-of-travel data provided <br />by the MWRD so that measurements made at the <br />upstream and downstream ends of the reach occurred <br />at about the same time on the hydrograph. For exam- <br />ple, if the upstream measurement was made at the <br />peak of daily stage fluctuations, the downstream <br />measurement wa.~ timed so that it also was made <br />at the peak of daily stage fluctuations. The time <br />lag between discharge measurements made at the <br />upstream and downstream ends of each segment were: <br />(I) 3 hours between 64th Avenue and 88th Avenue; <br />(2) 4.5 hours between 104th Avenue and Brighton <br />Ditch; and (3) 3.5 hours between 160th Avenue <br />and Highway 52 (Todd Harris, Metro Wastewater <br />Reclamation District, written commun., 1992). <br /> <br />Direct measurements of ground-water discharge <br />were made from August 1992 through January 1993 at <br />the 30 cross sections listed in table 2 using the follow- <br />ing techniques: <br /> <br />1. Five piezometers were installed at each of the <br />30 cross sections so that one piezometer was <br />located in the river channel 10ft from each <br />bank, one piezometer was located in the middle <br />of the channel, and one piezometer was located <br />between each of the outside piezometers and <br />the piezometer located in the middle of the <br />channel. The piezometers had carbon-steel <br />casings with 1 ,5-in inside diameters and 6-in <br />screens; the piezometers were installed so that <br />the middle of the screen was 1 ft below the <br />sediment/water interface. Each piezometer <br />was pumped at a rate of 0.25 gal/min until the <br />discharge water was clear (usually within <br />5 minutes), at which time pumping was <br />stopped and water levels allowed to equili- <br />brate. Water levels were allowed to equilibrate <br />for at least 15 minutes even though preliminary <br />tests indicated that equilibration was usually <br />achieved within 5 minutes. <br /> <br />Table 2. Looation of cross-section sites at which ground- <br />water discharge was measured <br /> <br /> Distance Distance <br /> downstream downstream <br /> from the from the <br />Cros&- Metro Cross- Metro <br />section Wastewater section Waeteweter <br />number Reclematlon number Reclamation <br /> District District <br /> effluent outfalls effluent outfalls <br /> (mllee) (miles) <br />1 0.2 16 11.7 <br />2 1.2 17 12.4 <br />3 2.1 18 13.8 <br />4 2.5 19 14.2 <br />5 2.8 20 14.8 <br />6 3,1 21 16.8 <br />7 3.4 22 18.0 <br />8 4.3 23 19.0 <br />9 4.9 24 19.9 <br />10 5.5 25 21.6 <br />11 6.7 26 22.0 <br />12 7.5 27 22.5 <br />13 8.5 28 23.1 <br />14 10.5 29 23.7 <br />15 ILl 30 24.6 <br /> <br />6 Quantity and Quality of Ground.Water Discharge to the South Platte River, Denver to Fort Lupton, Colorado, <br />August 1992 Through July 1993 <br />