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2023-12-26_GENERAL DOCUMENTS - C1981044
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2023-12-26_GENERAL DOCUMENTS - C1981044
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1/9/2024 3:25:31 PM
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DRMS Permit Index
Permit No
C1981044
IBM Index Class Name
General Documents
Doc Date
12/26/2023
Doc Name
Proposed Decision and Findings of Compliance
Type & Sequence
RN8
Media Type
D
Archive
No
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Page 18 of 27 <br /> the Twentymile Sandstone. <br /> 4. Mining in the 5 and 9 Mines was not expected to significantly impact the only domestic <br /> well near the permit area that may be completed in the Twentymile Sandstone (Lux <br /> well). The predicted drawdown of this aquifer where the well is located would not <br /> significantly impair the usefulness of the well. <br /> 5. Mining,mine dewatering discharge would cause a net increase in stream flow in the <br /> Williams Fork River. <br /> 6. Underground mining in the Williams Fork Mines was not expected to directly affect <br /> ground water in the Williams Fork River alluvium. <br /> 7. Underground entries in the Williams Fork Mines located beneath alluvium would not <br /> directly affect ground water in the Yampa River alluvium. <br /> 8. Development mining beneath the Big Bottom alluvial valley floor of the Yampa River <br /> would not impact the alluvial valley floor. <br /> 9. During mining of the 5 and 6 Mines,underground mine discharge from those mines, <br /> combined with spoil spring discharge from the Strip Pit,would increase dissolved <br /> solids concentration in the Williams Fork River. During low flow of the river and <br /> assuming worst-case mine discharges,the concentration was expected to increase by <br /> 224 mg/l, from the historical mean of 332 mg/1 to 576 mg/l. SAR was expected to <br /> increase from the historical mean of 0.44 to 5.05. The Williams Fork River would have <br /> a medium salinity hazard during low flow and would have a low to moderate sodium <br /> hazard at other times. Based on past discharges,the worst-case discharges were not <br /> expected to be reached therefore,the medium salinity hazard was not expected to be <br /> achieved. Impacts from dissolved solids loading of the Williams Fork during irrigation <br /> season would be minimal due to dilution resulting from high river stage. <br /> 10. At this point all the mine pumps are shut off, and the water levels in the 45 and#6 <br /> Mines are gradually rising. It is estimated that at the end of the life of the mine, it may <br /> take on the order of 16 years for the mines to completely fill. At the writing of this <br /> document,the pumps are permanently shut off. <br /> 11. After the 45 and 46 Mines refill,water may seep from the coal subcrop into the <br /> Williams Fork alluvium. The seepage would be driven by a maximum pressure <br /> developing in the subcrop equal to a head of 100 ft. above the ground surface. This <br /> head would cause maximum seepage of 20 gpm. In a worst-case scenario,the 19.5 <br /> gpm discharge would raise SAR in the Williams Fork River alluvial water from the <br /> historical mean of 3.6 to 9.4. The alluvial water is naturally higher in dissolved solids <br /> and metals than the mine discharge water;therefore,increased SAR is the only <br /> Williams Fork Mines Prepared by: R ReiRey M.S. GISP <br /> C1981044 December 2023 <br />
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