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Surface Water Site SW-S2-6 (99C3). This site monitors Cov Casip Creek less than 1/4 mile downstream Of tRe NPDES 004 dischar acent diversion ditch e I d d Review of the • . g j n an a historic hydrograph indicates a higher peak anovpack rvnoff than last year. Peak floes at this site have been reduced further by tRe reduction of the disr2~arge culvert diameter sn 1937 at the NPDES 004 site discussed earlier. Beview of the TDS plot indicates an increasing trend due to eater from NPD88 009. Surface Water Site SW-52-30 (SSC10). The site monitors Cov Carte Creek at its confluence with Fish Creek. It is monitored Hay through September on a monthly basis. This site flows less often than the upper Cow Camp Creek at Site 6. This year, no flow was present at this site on the Scaly through September monthly V191t9, although Site 6 was £lovinq continuously those months. This reduction in floe is Que to stream channel infiltration, evapotranspiration, and the absence of lateral inflow from tributaries to Cow Camp Creek. The TDS plot reveals no definite trend. HPDES Discharge Point 008. The annual average floe (from weekly measurements) since this pond began to flow are: 1995 = 0 .337 cfs 1994 = 0 157 cfs • . 1993 = 0 .332 cfs 1992 = 0 .132 cfs 1991 = 0 .112 cfs 1990 = 0 .067 cfs 1989 = 0 .103 cfs 1938 = 0 .104 (reserwiz did not completely fill until February 25, 1933). Beviev of the above table shoxs that the average discharge was greater than all previous years. Beviev of the hydrograph indicates that this year's peak flow was the second highest on record. Review of the TDS plot indicates an increasing trend. Surface Water Bite SW-92-12 (SSB12). Thie site monitors Bond Creek at its confluence with Fish Creek. It is monitored May through September on a monthly basis. As vas noted also at the lower Cow Camp Creek SSte 30, this site flows less often than the upper Bond Creek site, NPDES 003. Floe vas observed at Site 12 during the Hay through July visits, r1 L 10