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• {h dttduw: Uw/ l,~rrrprrr/riun wrd lnipucr aeer_.,ninu fur drr Ycnnir /rrd: ldl/rnu aruc . <br />withdrawal was L?0,779 gpd fur_llll working Vacs. .I ~ estimated to hace been 74 acre lest. <br />This decrease in usage can he attributed «~ c~m- <br />pletion of surface construction projects (water was The quality- u( mine water is considered gaud and <br />used for dust control, compaction, concrete pro- offers no problem for treatment and discharge. <br />duction, etc.). Mine water was primarily discharged from the <br />Water from the freshwater pond(s) is used in two <br />ways. It can be treated to meet potable and sani- <br />tary water requirements, used, and then treated as <br />sanitary waste water. Or, it can ha withdrawn for <br />dust suppression in the mine. in which case it then <br />becomes mine water. <br />MCC's Mt. Gunnison pipeline water rights were <br />out of priority during a portion of water vear 1991 <br />between Julv 23, 1992 and October 1. 1992. Aver- <br />age daily low tluw in the North Furk during water <br />year 1992 was 347 cfs. The maximum withdrawal at <br />the intake is 450 gpm with both pumps operating. <br />This is about 0.3 percent of thz ohsened a+crage <br />daily low flow in the river durine the water }car. <br />Sanitary Waste Water <br />The sanitary waste water treatment plant has been <br />• operating since the fall of 193?. During water year <br />1992, discharge from the plant a+eraged 0.0043 cfs. <br />This discharge is approximately 0.0012 percent of <br />the average daily flow of 347 cfs observed in the <br />North Fork during the year. <br />Discharge monitoring results from the waste water <br />treatment plant, conducted under NPDES Permit <br />Nu. CO-0033776, are included in Appendix J. <br />There were two isolated incidents of effluents <br />exceeding permit limitations. During monitoring <br />period 1 October - 31 December 1991, actual <br />residual chlorine reached Q6~ vs. permit limitation <br />of 0.5; and during 1 July - 30 Szptember 1992 <br />actual total suspended solids was 76.4 cs. a permit <br />limitation of 45. Both incidents appear to be <br />exceptions as the parameters were within limits at <br />all other times. Thc results of the analyses suggest <br />the waste water discharge has nu measurable effect <br />on water quality in the North Fork Gunnison <br />River. <br />Mine Water <br />Mine inflows during water year 1992 were small. <br />The total mine water inflow was 63? acre (ect <br />during the year. The total water exiting the mine is <br /> <br />Nu. 2 Portal. Nu discharces occurred from Sylves- <br />ter Gulch or Portal No. 5. <br />Mine water inflow for water year 1993 is cxpceted <br />to be Icss than that experienced during water ccar <br />1992. Onl_v the amount of water necessary (or <br />mining will be imported into the mine. Mine water <br />is expected to have water quality characteristics <br />similar to that reported in Table ?. <br />Because of the small quantity of mine water <br />anticipated, any discharge from ponds would <br />normally he dominated by water quality character- <br />istics u( disturbed area runoff as described in the <br />following section. <br />Runoff from Disturbed Area <br />Overland runoff from snowmelt and precipitation <br />within the disturbed areas is routed to one u( six <br />sediment ponds on the mine site. The six sediment <br />ponds are designed to contain the predicted runoff <br />from a statistically determined l0 year, 24 hour <br />precipitation event as well as a calculated sediment <br />storage volume. The ponds arc also designed to <br />pass the overflow from a 3~ year. 24 hour prccipi- <br />tatiun event safely. <br />The West Elk Mine site receives much ul us <br />annual precipitation from snowfall during the <br />winter months. When warmer weather begins in <br />late February, March or April, most runoff to the <br />sediment ponds is from snowmelt. It is emirely <br />possible (or a volume of runoff greater than the l0 <br />year, 24-hour precipitation event to result from <br />snowmelt or snowmelt coupled with a small precip- <br />itation event. <br />The sediment ponds are treated with cationic <br />flocculent when necessary w speed clarification <br />and settling of suspended solids. The ponds MB-1, <br />MB-2, MB-5, and MB~i have manually controlled <br />dewatering devices. Ponds MB-3 and MB-4 have <br />automatic dewatering capabilih-. Ponds MB-l. <br />MB-'_, MB-= and MB~i are dewatered intermit- <br />tently with most discharges coming during early <br />spring runoff. Dewatcring procedures take usually <br />l2 <br />