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2020-03-24_PERMIT FILE - C1981019A (2)
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2020-03-24_PERMIT FILE - C1981019A (2)
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Last modified
5/11/2020 5:24:59 PM
Creation date
5/9/2020 2:50:43 PM
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Template:
DRMS Permit Index
Permit No
C1981019A
IBM Index Class Name
Permit File
Doc Date
3/24/2020
Type & Sequence
TR135
Section_Exhibit Name
Rule 2 Permits -ST
Media Type
D
Archive
Yes
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RULE 2 PERMITS <br />2.05.6 (3)(b)(i & ii) Hydrologic Controls <br />Surface water and groundwater drainage from the mining areas will be controlled as described in Section <br />2.05.3(4) and Section 4.05.Surface water flow will be diverted around the mining operations and into <br />sediment ponds. Stormwater that enters the mining operations and water that occurs on the mining <br />operations will be allowed to evaporate or infiltrate, or will be routed into these surface structures. <br />2.05.6 (3)(b)(iii) Probable Hydrologic Consequences <br />Rule 2.05.6(3)(b)(iii) requires determination of probable hydrologic consequences for the mining <br />operations. This rule indicates that these consequences must be defined for both the permit area and <br />adjacent areas, for quantity and quality of surface and ground waters. Baseline conditions must be <br />established, and possible impacts from the activities must be anticipated. <br />Summary of the Probable Hydrologic Consequences — South Taylor Pit <br />The anticipated probable hydrologic consequences of mining coal in the South Taylor area are: <br />• Springs near the South Taylor Pit might experience increased and/or decreased flow. <br />• The South Taylor pit will eliminate several seeps and springs. <br />• Dewatering of the pit is not anticipated. <br />• Hydraulic transmissivity within the backfilled pit will be higher than the adjacent unmined areas. <br />• Base flow in Good Spring Creek will be reduced by up to 7% during and for 45 years after <br />mining. <br />• Total dissolved solids in the base flow of Good Spring Creek will increase by 1.6% to 13.5% for <br />several hundred years after mining has been completed, with sulfate the dominant increasing ion. <br />• Base flows of Taylor Creek will not be reduced, and peak flow of Taylor Creek will be reduced <br />2% by the South Taylor pit. <br />• No other statistically significant changes to surface water quality or quantity are anticipated. <br />These consequences are discussed in the following subsections. <br />Potential Impacts to Springs and Seeps <br />Springs in the Colowyo Mine area result from three general sources: 1) typified by a relatively deep soil <br />accumulation immediately upslope and shallow bedrock downslope of the point of discharge, 2) discharge <br />within valley bottom deposits, and 3) from sheer bedrock faces on hillsides (CDM 1985b). The first two <br />of these sources may mask or contribute to bedrock sources of the springs. The seeps and low volume <br />springs flow generally in response to snowpack accumulation and subsequent melting resulting in <br />seasonal flows. A total of 8 springs, which maintained flow for the month of July, contribute to base <br />flows in the receiving streams adjacent to South Taylor, and were determined as a critical component of <br />the hydrologic balance. Seeps and springs relevant to this permit revision are shown on Map 10. <br />The majority of the springs, with bedrock sources, appear to be contact springs. A contact spring results <br />from the infiltration of water from the surface to a porous zone (such as sandstone) above a horizontal <br />hydrologic barrier (such as shale) where the water preferentially flows along the contact to the exposure. <br />This type of spring is common in areas where alternating sequences of lithologies exist that exhibit <br />differential hydraulic conductivities, such as the Williams Fork Formation. <br />South Taylor/Lower Wilson — Rule 2, Page 79 Revision Date: 4/7/17 <br />Revision No.: RN -07 <br />
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