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1997WY (Water Yeaz) - 0.506 cfs <br />1996WY - 0.609 cfe <br />1995WY - 0.357 c!e <br />1994WY - 0.121 c!e <br />1993WY - 0.360 cfe <br />1992itt - 0.131 cfs <br />1991WY - 0.189 c!e <br />1990WY - 0.135 cfs <br />1989WY = 0.214 c!e <br />1988WY 0.180 cfe <br />19S7WY = 0.110 cte <br />1986WY 0.294 cfe <br />1985CY (Calendar Year) - 0.357 eta <br />1984CY = 0.447 cfe <br />1983CY - 0.154 cts (reservoir did not completely Pill until <br /> Hazc2t 7, 1983) ~ <br />Review o! hydrographs and the above table chows that for this year, Elora ware the second <br />highest on record. 11eo affecting floc from the 004 pond is the reduced diameter of the <br />discharge culvert modified on Nay 29, 1987 (36 inches to 6 inches). <br />Reviar of the TD9 plot indicates that TDS values haw consistently increased since 1982 <br />primarily due to a concurrent increase in upgradiant mined area and ground rater <br />reeaturation in the epoile. <br />9urfaca Water Sita SW-32-6 (SSC6). This Bite monitors Cor Camp Creek lees thm 1/4 mile <br />i dornetraam of the NPDES 004 discharge. Raviar of the historic hydrogzaph indicates the <br />third highest peak floc on reeosd. Peak flora at this site have bean seduced further by <br />the seduction of the disUarge culvert diametmr in 1987 at the NFDES 004 site discussed <br />eazlier. Reviar of the TDS plot indicates an increseinq trend due to rater from NPDES <br />006. Monitoring at this site was discontinued in June (sea "Introduction"1• <br />Surface Water Site SW-92-10 (SSC10). The site monitors Cor Camp Creek at its confluence <br />rith Fish Creek. It is monitored May through September on s monthly basis. This year, no <br />flow ras present at this Bite on the July and septamber monthly visits, although MPDES 004 <br />was floring continuovely thoea months. This reduction in floc is due to stream cliannal <br />10 <br />