Laserfiche WebLink
West Elk Mine <br />If surface cracks were to form and if they were to intercept stock ponds or ephemeral channels, they <br />could potentially intercept surface water. Field evidence at the Section 17 cracks, evaluation of the <br />soft plastic shales occurring in the Barren Member above the F Seam, and theoretical subsidence <br />stress-strain relationships discussed elsewhere in the subsidence section of the application, each <br />strongly suggest that surface cracks would not extend to any great depth. <br />Two factors will also tend to heal the cracks, if they were to intercept water. First, the shales of the <br />Mesaverde Formation are known to have shrink-swell capacity. If the saturation of these shales <br />were to be increased, they would swell and this could be expected to help heal the crack. Secondly, <br />Mr. Jeff Hynes of the Colorado Geological Survey (1994) has stated that a greater factor in crack <br />healing would be increases in the plasticity of the shales as water saturations were increased. Simply <br />stated, as the shales become wetter, they soften and will squeeze into and heal the cracks. <br />An important consideration regarding mining in the Apache Rocks, South of Divide and Dry Fork <br />permit revision areas are potential impacts to the Minnesota Reservoir. The water rights <br />implications of mining in the tributary area to the reservoir are discussed later in Section 2.05.6 <br />(3)(b)(iii & viii) Water Rights. MCC has committed to maintaining a buffer zone between active <br />mining and the dam of over 1,000 feet, which is greater than the distance utilizing the conservative <br />angle of draw 25 degrees. With a setback of this margin, there is no risk of either a crack <br />developing under the reservoir or aggravation of the existing structural problems with the dam as a <br />result of MCC's mining activities: Mining of longwall Panel 13 in the B Seam occurred at a <br />distance of approximately 700 feet from the reservoir with no adverse impacts to the <br />structure. The additional distance for longwall Panel E9 is very conservative given that the E <br />Seam is stratigraphically higher and, therefore, has a smaller area of influence at a given <br />angle of draw. <br />Wetlands <br />Based upon inspection of conventional and infrared aerial photographs and reconnaissance-level <br />field investigation, the wetlands in the permit area are confined primarily to manmade stockponds in <br />the drainages. They are intermittent in nature. Very few "natural" riparian wetlands are evident. <br />The total acreage of potential jurisdictional wetlands in the permit area is approximately 7 acres (as <br />defined by the U.S. Army Corps of Engineers (USACE)). Field surveys conducted in August 1995 <br />verified this estimate. An additional 2 to 3 acres lies above the LONE and 11 NE longwall panels. <br />Field surveys in the South of'Divide permit area in 1996 found additional wetland/riparian <br />areas along the valley bottoms within the Dry Fork and Lick Creek drainages and in <br />association with hillside spring and seeps (refer to Section 2.04.10). Another study was <br />conducted November 2004 shoving these additional wetland areas and is included in Exhibit 32B, <br />Drawing 1. <br />AlthouUh most of the wetlands are found u1 drainage channels, there are small, isolated wetlands on <br />*he hillsides where springs and seers emerge. There are other isolated wetlands in association with <br />landslides and slumps. In these instances. the wetlands are associated with the uppermost portion of <br />the landslide/slump, where a relatively flat area has been created and water has tended to collect and <br />saturate the soils. <br />2.06-207 Revised June 2005 PRIO: Rev. Alarch 2006: Rev. April 2006 PRIO; .May 2006 PRIO; Sep. 2007 PR12; Feb 2008 PR12