Laserfiche WebLink
-44- <br />Cumulative Hydrologic Impact Assessment - Surface Water (Cont'd) <br />Seepage from Waste Rock/Coal Refuse Piles <br />The North Fork region contains several historic, existing, or proposed waste rock/ <br />coal refuse piles. The Mt. Gunnison Mine facilities includes a small waste rock <br />pile ( I acre) with a larger pile of approximately 10 acres anticipated in the <br />future. The Orchard Valley Mine has an existing waste rock pile (5 acres), and <br />Western Slope Carbon has recently reclaimed a small waste rock pile ( 9 acres). <br />The Somerset life-of-mine area includes two historic waste rock/coal waste disposal <br />areas. The Hubbard Creek site was used from 1970 until 1977. Tyre East Yard site <br />( 9 acres) was used as a cvaste dump prior to 1969, but is currently part of the <br />surface facilities area. All future waste rock at the Somerset Mine will be <br />disposed of underground, or at a waste disposal site to be established at the <br />area of the "C" seam mine portals (1.2 acres) after the final sealing of these <br />portals. <br />Most of these waste rock/coal refuse piles are located in areas away from the North <br />Fork stream - alluvial aquifer system, and seepage could reach the stream - <br />alluvial aquifer system only after considerable dilution. Two sites, however, the <br />Somerset East Yard, and western Slope Carbon's Crystal Meadow site are adjacent <br />to streams, where seepage from the piles might enter the stream - alluvial aquifer <br />system. <br />The effects of the waste piles on flow in the North Fork of the Gunnison can be <br />evaluated using the mass balance - mixing model shown above. This requires estimating <br />the total dissolved solids concentration of the Ieachate from the pile and estimating <br />the rate of discharge to stream - alluvial aquifer systems. The total dissolved <br />solids concentration can be estimated by using a concentration based on analyses <br />of spoil waters in other parts of the state, 3,000 mg/1. The chemistry of the <br />leachate would probably be a sodium-bicarbonate type water with relatively low total <br />metal concentrations. The rate of discharge can be estimated from the water balance <br />provided in the Orchard Valley permit application. This water balance estimated <br />subsurface runoff to be 2.8 in/yr. Assuming that most of the water for subsurface <br />flow and deep seepage is the result of snowmelt, it may be that this discharge <br />is limited to a 60-day period, the rate of discharge can be calculated. <br />(13 acres surface area) x (2.8 in.)(1/12) - 3 acre-feet water. <br />(3 acre-feet) x 43,560 ft3/acre-feet ? 60 days r 24 hrs 3 60 min/hr ~ 60 sec/min = <br />0.03 cfs day <br />Using an estimated concentration of 3,000 mg/1 and an estimated discharge of 0.03 <br />cfs, the effects of the waste rock piles and mine water drainage upon the North <br />Fork of the Gunnison under average flow conditions can be estimated. <br />Cd (432 cfs)(95 mg/1) + (0.25 cfs)(3,500 mg/1) + (0.03 cfs)(3,000 mg/1) <br />432 + 0,02 + 0.03 <br />Cd = 97.2 mg/1 <br />This results in a 2.2 mg/1 increase over baseline conditions, which is insignificant. <br />In addition, it is probably an overestimation, since seepage in the piles is the <br />result of snowmelt and would probably occur when stream flows are much higher than <br />average. <br /> <br />