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infiltration, evapotranspiration, and tha absence o! lateral ..,slor from trlbutaziae to <br />• Cor Camp Creak. The TDS plot reveals an increasing trend. <br />MPDES Discharge Point 008. The annual average floc (from xeakly measurements, !or the <br />rater year) since this pond began to floc axe: <br />1997 0.606 cfs <br />1996 0.479 cfs <br />1995 0.337 cLe <br />1994 ~ 0.157 c!s <br />1993 = 0.332 cfs <br />1992 ~ 0.132 cis <br />1991 = 0.112 cfs <br />1990 0.067 cts <br />1989 = 0.108 efe <br />1988 0.104 (reservoir did not completely fill until February 25, <br /> 1988). <br />Reviar of tha above table shore that the average discharge rae greater than ell previous <br />• years. Raviar of the hydrograph indicates that this yeaz's peak flow rae the second <br />highest on record. Reviar of the TDS plot indicates an increasing trend. <br />Surface Water Site SK-52-12 (SS812). This site monitors Bond Creek at its confluence with <br />Fish Creek. It ie monitored May through September on a monthly basis. This Bite nozmally <br />flora lase often than the upper Bond Creak site, HPDES 008, although floc was obearwd at <br />Site 12 during all visits this year due to high rainfall. The TDS plot seems to indicate <br />a slightly increasing trend. <br />Surface Slater Site SW-S2-11 (SSF11). This site monitors Fieh Creak upstream of its <br />confluence oP Cor Camp Creek. It ie monitored May through September on a monthly basis <br />but only if either Sites 10 or 12 aza florinq. This Bite ie upstream oP Senaea II Hine <br />discharges. <br />Surface Water Sita SW-S2-13 (39F13). This site monitors Fiah Creek doxnstream of its <br />confluence rith Bond Creak. it ie monitored at the same fraquenry ae Site 11. TDS values <br />st Site 13 rare 85 to 127 percent of those observed at Site 11. <br />11 <br />