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PERMFILE118274
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PERMFILE118274
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Last modified
8/24/2016 10:13:57 PM
Creation date
11/25/2007 5:00:11 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1980007A
IBM Index Class Name
Permit File
Doc Date
11/16/2006
Section_Exhibit Name
2.05.5 & 2.05.6 Post-Mining Land Uses and Mitigation of Surface Coal Mining Operation Impacts
Media Type
D
Archive
Yes
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West E[k Mine <br />• percent (0.002) and there is no measurable risk of long-term surface cracks in the internal portions <br />of panels, based on MCC's mining experience to date. Furthermore, the crack connection would <br />need to stay open and clear for long enough to impose a measurable hydrologic change, and this is <br />highly unlikely given the subsurface changes that will be occurring in the aftermath of longwall <br />mining. <br />In a hypothetical situation where a connection were established, the stream channels in question <br />have small drainage basins with average annual surface flows of approximately 200 acre-feet per <br />square mile per year. Cracks will close via "healing" and "sealing," as discussed in response to <br />other questions. <br />These calculations are substantiated by the actual mining experience at West Elk Mine. For <br />example, during the unusually wet late spring and summer of 1995, there were no increased inflows <br />to the longwall panels beneath Gribble Gulch and Lone Pine Gulch. Also, as stated in the October <br />24, 1994 CDMG Decision Document on the Jumbo Mountain Tract (see page 31), "A direct <br />fracture connection to the mine was not established in Lone Pine Gulch under a cover as low as 120 <br />feet (when F Seam mining was occurring)." Similarly, mining of the B East Mains beneath <br />Sylvester Gulch did not produce a connection with the surface. The groundwater emanating from <br />the B East Mains fault had, and continues to have temperatures in excess of 80°F. This combined <br />with the lack of tritium, 14C and 180 isotopes, (Mayo 1998) indicates this water is not connected to <br />local surface waters. <br />• Additional considerations regazding surface water effects include the following: <br />1. Mining in the Apache Rocks permit revision area will not measurably impact the surface water <br />hydrologic balance of the Dry Fork of Minnesota Creek. Based strictly on surface acreage, this <br />area contributes only 22 percent of the Dry Fork of Minnesota Creek drainage basin flows as <br />measured above the Lower Dry Fork gage. Because the azea is on asouth-facing slope, <br />however, the actual percentage of surface runoff will be lower. MCC's 1986 Minnesota Creek <br />Augmentation Plan, Case No. 86CW38 (approved by the Colorado Water Court), provides for <br />total replacement of the annual streamflow generated in the Dry Fork basin. For these reasons, <br />impacts to the Dry Fork of Minnesota Creek will be minimal due to B and/or E Seam mining. <br />2. Mining in the Box Canyon permit azea will not measurably impact the surface water hydrologic <br />balance of the North Fork. As previously stated, 100 percent of the mining area has a B Seam <br />overburden thickness of more than 500 feet, thus all but eliminating the possibility of surface <br />water capture by the mine workings. <br />3. Based on the B Seam mining plan, in the current permit, which includes the Box Canyon pernut <br />revision area, it is not anticipated that there will be direct mining impacts to Sylvester Gulch. <br />In summary, based on the small amount of surface flow that occurs annually, the low probability <br />of surface cracking due to subsidence, and the depth of cover and the character of the overburden <br />materials within the permit area, the projected mine subsidence will not significantly impact the <br />• streams. <br />2.05-194 Revised Jvne 2005 PRIO, January 2006, March 2006; Rev. May 2006 PRI G <br />
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