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i <br />resemblance to the quality of water found in the wells of the overlying coal seams. The <br />applicant concluded that the seep appeared to be emanating from the bum zone <br />overlying the uppermost entry. The source of the water was most probably recharge <br />from snowmelt and runoff The seep had an average yield of 2 gpm. Since pumping <br />ceased, the water in the mine has stabilized at approximately 20 feet below the portal <br />level at the surface. To date, there has been no discharge from the mine portal. <br />No springs or seeps were located within the life-of--mine permit boundary. A perennial <br />seep exists along the base of the Grass Valley Reservoir. The seep has an average flow <br />of ~ gpm. Seeps along the base of the reservoir create the perennial flow in the Harvey <br />Gap Drainage during period when no water is released from the reservoir for imgation. <br />This source of water is isolated from the mine by the impervious Mancos Shale. <br />The extraction of coal has ceased at the mine, and the mine portals sealed and covered. <br />The hydrostatic water level in the mine has apparently stabilized. The E-coal seam is <br />of low permeability, and is isolated by more impervious layers. The mine water quality <br />was representative of water of the coal seam. The only water apparently introduced to <br />the mine (near the portals) was of higher quality (perhaps surface water reaching the <br />mine through bum azeas). As the water level in the mine appears to have stabilized, the <br />Divisions finds that the mine has no impact on the quantity of ground water in the <br />potential aquifers of the area (no depletion, and apparent stabilized recharge). As the <br />water quality in the mine is representative of the water in the water of the coal seam, <br />perhaps improved slightly due to surface recharge, the Division finds that the <br />application poses no impact on the quality of ground water in the potential aquifers of <br />the area. <br />The potential for diminution or degradation of ground water in the bedrock aquifers <br />overlying the mined coal seam is small. This is due to: (1) the small size of the mine, <br />(2) the lack of communication of the coal seam with overlying beds due to interbedded <br />shale layers, and (3) the lack of potential of the rock strata within the affected'section <br />to supply a high quality ground water resource. However, although the water quality <br />in the overlying bedrock aquifers is poor, those aquifers are used for domestic supply <br />in the vicinity of the mine. Additionally, mining-related subsidence has the potential <br />to create fractures in the interbedded shale layers between the mined coal seam and the <br />aquifers. Although the existing domestic wells lie outside the angle of draw for the <br />mine, subsidence-related fractures could create communication between the aquifers <br />and the coal seam, thereby disrupting the recharge zones for these aquifers, which <br />could result in the diminution of water supply of current users. However, the operations <br />proposed by the application to not aggravate such potential impacts (none noted to <br />date) from operations approved for previous terms of the permit. <br />There has been no surface water discharges from disturbed areas of the mine. Soils of <br />disturbed areas are not toxic or acid forming. The seep from the Grassy Gap Reservoir <br />is isolated from surface waters of the mine workings by location (the seep is upstream <br />of the mine). The drainage thalweg is in an incised valley at an elevation <br />approximately sixty feet below disturbed surface areas of the mine. Ground waters of <br />the mine workings are isolated by impervious formations. There is potential for <br />14 03/06/00 <br />