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r <br />-46- <br />The ground water assessment indicates that mining may affect several <br />aquifers in the general area. The Trout Creek sandstone, Tow Creek <br />sandstone, and Twentymile sandstone would not be affected by the Foidel <br />Creek Mine. The Middle Coal Group aquifer may be affected by the Foidel <br />Creek Mine, as well as by other mines in the area. During mining <br />operations, ground water flow in this aquifer would be diminished. This <br />effect is not significant because no wells are completed in this aquifer <br />in the Twentymile Park Basin, and any loss of ground water contribution <br />to surface streams is expected to be minor. Following mining and <br />reclamation, ground water flows would return, but water of degraded <br />quality may discharge to surface systems. This effect was included in <br />the surface water model. Mining may affect the quantity and quality of <br />flow in alluvial aquifers. Changes in water levels in the alluvium are <br />not expected to be significant, and the expected water quality <br />degradation would probably not limit pre-mining water uses. <br />In lower Piiddle Creek, stream flaw and total dissolved solids <br />concentrations would increase primarily as the result of discharge from <br />the underground mine workings. Water from Middle Creek is used for <br />irrigation. However, as shown on Map 14a, water is diverted upstream of <br />the reach that would be affected by mining. The proposed Foidel Creek <br />underground mine would have no adverse effect upon water use in this area. <br />Water from Fish Creek is also used for flood irrigation. The model <br />indicates that the total dissolved solids concentrations would exceed the <br />use criteria (1000 mg/1) during the low flow months (August, September) <br />of dry years. During these periods, the water in effected reaches of <br />Fish Creek may be unsuitable for flood irrigation use. However, the <br />actual effects would not be expected to be as great as the model <br />predicts, In the model, the long-term effects of mining, primarily <br />discharge of affected ground water, are directly added to surface flows. <br />In reality, ground water discharge is to the stream/alluvial aquifer <br />system. Flow in the alluvial aquifer would help to buffer the effects of <br />mining. Both surface and alluvial ground water quality would be <br />degraded, but surface flows would not be affected to the extent predicted <br />by the model. Given the uncertainty in the prediction of long-tens <br />effects, the water quality on Fish Creek is still within acceptable <br />limits. However, it appears that affected water quality is approaching a <br />total dissolved solids concentration beyond which water use may be <br />limited. <br />Lower Trout Creek and the adjacent Yampa River are used for both flood <br />irrigation and domestic water. The projected effects of mining would not <br />limit these uses. <br />The cumulative hydrologic assessment indicates that, with the proposed <br />hydrologic stipulations, the proposed mining operation has been designed <br />to prevent material damage to the hydrologic balance outside the permit <br />area. <br />