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<br />2' <br />o <br />00 <br />a: <br />;) <br />Sla: <br />2w <br /><(f- <br />Cl::J <br />a: a: <br />Ow <br />-Ie.. <br />~CIl <br />0:; <br />f-;;!i <br />u.Cl <br />0_ <br />2:] <br />0- <br />-:; <br />~~ <br />f- <br />2 <br />w <br />U <br />2 <br />o <br />U <br /> <br />-.- McKay Road <br /> <br />-e- Henderson <br /> <br />-,A.- Road 8 <br />Road 81N1B Line indicates average <br />concentration of total <br />organic carbon in <br />ground water, name <br />refers to wells in table 3 <br /> <br /> <br />10 <br /> <br />. <br /> <br />8 <br /> <br />,A. <br /> <br />e <br /> <br />6 <br /> <br />McKay Road .. <br />1A/1B <br /> <br />4 <br /> <br />Road 8 1A11 B <br /> <br />Henderson 1A11B <br /> <br />2 <br /> <br />o <br /> <br />20 <br /> <br />. <br /> <br />.- <br /> <br />e <br /> <br />- <br /> <br />-,A. <br /> <br />40 <br /> <br />60 <br /> <br />80 <br /> <br />100 <br /> <br />DEPTH BELOW SEDIMENTIWATER INTERFACE, INCHES <br /> <br />Figure 16. Concsntratlons of total organic carbon In ground water with dspth below the sedlmsnllwatsr Interfacs <br />at McKay Road, Hendsrson, and Road 8, Samplss at McKay Road, Hsnderson, and Road 8 were collscted on <br />October 1, 1992; October 5, 1992; and Ssptembsr 25, 1992, respsotlvsly. Valuss for surface water Indicated at a <br />depth of 0 Inchss below the sedlmsnllwater Intsrface. <br /> <br />Concentrations of dissolved nitrite plus nitrate, <br />ammonium, and phosphorus in water samples from the <br />piezometers at the 30 cross-section sites ranged from <br />less than 0.01 to 8.98 mgIL as nitrogen, less than 0.1 to <br />15.3 mgIL as nitrogen, and 0.28 to 7.22 mgIL as phos- <br />phorus (table 9). The median concentrations of dis- <br />solved nitrite plus nitrate, ammonium, and phosphorus <br />were 1.22 mgIL as nitrogen, 1.7 mgIL as nitrogen, and <br />1,41 mgIL as phosphorus. Concentrations of nitrite <br />plus nitrate in ground water below the sediment/water <br />interface increased with distance downstream from the <br />MWRD plant, whereas concentrations of ammonium <br />decreased (fig. 17). Concentrations of phosphorus <br />showed no consistent pattern of change with distance <br />downstream from the MWRD plant. The pattern of <br /> <br />concentration changes observed for nitrite plus nitrate <br />and ammonium with distance downstream from the <br />MWRD plant is similar to what has been observed in the <br />river. The pattern of concentration changes in the river <br />is generally attributed to the addition of ammonium to <br />the river from the MWRD plant, followed by the conver- <br />sion of ammonium to nitrate by nitrifying bacteria as the <br />water flows downstream. Due to the movement of sur- <br />face water into and out of the bed sediments, it is likely <br />that at least part of the concentration pattern of nitrite <br />plus nitrate and ammonium observed in the small-area <br />flow system (fig, 17) is the result of similar processes. <br />However, other processes also were active in the small- <br />area flow system. <br /> <br />30 Quantity and Quality of Ground-Water Dlscharga to tha South Platte River, Danver to Fort Lupton, Colorado, <br />August 1992 Through July 1993 <br />