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-37- <br />Effects of Mining on Surface Water <br />The Mt. Gunnison No. 1 Mine plan is designed to minimize the impacts of <br />the project on the surface water hydrology of the region. Disturbed <br />area drainage is collected and treated on the site. Drainage from <br />undisturbed land is diverted around the site. Five sedimentation ponds <br />have been built for the surface facilities area. A system of lined <br />ditches convey water from the disturbed areas to the ponds. All five <br />sedimentation ponds discharge into the North Fork. The mine operation <br />has obtained the appropriate NPDES permits. Effluent quality for the <br />sedimentation ponds has been monitored to determine permit compliance. <br />The applicant will also continue monitoring of surface water to <br />determine the impact of mining on the hydrologic regime. <br />Runoff from both the Upper and Lower permanent waste disposal sites <br />will be routed through the sediment control system and must meet <br />effluent limitations. Final designs for the waste rock piles, which <br />include surface and subsurface drainage systems, allow for the <br />collection of water leachate from the pile. Analysis of sample rock <br />provided by WECC indicates that potential toxicity levels are below EPA <br />standards. Consequently, it appears that if runoff were to develop <br />from the waste piles, minimal impact will occur on the North Fork of <br />the Gunnison River. WECC will be monitoring both ground water quality <br />and levels under the piles, leachate quality and from the subdrains, <br />and spring quality from the base of the Upper permanent pile site if <br />constructed. <br />WECC estimated that treated waste water from the mine could reach <br />38,000 gallons per day. However, the annual reports from WECC <br />submitted to date indicate that discharges from fall 1983 to winter <br />1984 averaged about 2,000 gpd. This is about 0.01 percent of the low <br />flow of 20 cfs observed in the North Fork for that period. For spring <br />of 1984 the discharge averaged 7,000 gpm or 0.05 percent of the low <br />flow of 21,6 cfs observed on September 4, 1984. This indicates that <br />there is a great dilution occurring. This indicates that the discharge <br />is having little if any effect on river water quality. <br />The Mt. Gunnison Mine is not expected to significantly impact water <br />quantity in the North Fork Valley in the first five year permit term. <br />water used in the mine and for domestic purposes is supplied from the <br />North Fork River during higher flows when LAECC's water rights are in <br />priority. Also, limited mine water encountered from the workings will <br />be available for use by the mine. <br />WECC presented a projection of depletions to the Colorado River System <br />to quantify impacts on aquatic species. This information was requested <br />by the U.S. Fish and Wildlife Service (Windy Gap Study). The results of <br />WECC's study showed a net depletion of 13.1 ac-ft per year from the <br />North Fork of the Gunnison River. This is a small depletion in <br />relation to the size of the mine and in comparison to the flow in the <br />North Fork of the Gunnison River. <br />