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If there are no approved suitability criteria listed in these sources, the CDRMS recommended using <br />suitability criteria provided in the Wyoming Department of Environmental Quality (WDEQ) Guideline <br />No.1 Topsoil and Overburden Tables 1-2 Criteria to Establish Suitability of Topsoil and 1-4 Criteria to <br />Establish Overburden Suitability (WDEQ 1984) and Guideline No. 1A Topsoil and Subsoil Attachment B2 <br />Criteria to Establish Suitability of Soil or Soil Substitutes (WDEQ 2015). <br />Many of the geochemical parameters contained in the CMLRD 1982 Guidelines do not have suitability <br />criteria in either the Trapper Mine Permit or the WDEQ Guidelines. For these constituents, suitability <br />criteria provided in the Soil Conservation Society of America text Reclaiming Mine Soils and Overburden <br />in the Western United States - Analytic Parameters and Procedures (Williams and Schuman 1987) were <br />used for comparison. <br />Minino Methods <br />The overburden geochemistry should be evaluated in light of the mining methods used at the Trapper <br />Mine as these techniques result in considerable mixing of the spoils which homogenizes the bulk soil <br />chemistry. As described in Sections 3.1.5 and 3.5.1, TMI uses a "multiple equipment scenario" in their <br />mining and reclamation processes that results in topsoil being removed and stockpiled by scrapers, <br />followed by overburden being removed by trucks/loaders, dozers, and draglines. Unmined rider coal <br />seams or seams which are either too thin or have parting materials rendering them unsuitable for <br />mining are removed along with the overburden. The mineable coal seams are then removed by mining <br />and hauled to the power plant. <br />As a general rule, following topsoil removal all near -surface overburden above the H coal seam will be <br />stripped using a truck/loader mining method. This H overburden extends to a depth of approximately <br />49 feet and consists of the weathered geologic zone. All depths are referenced to the overburden drill <br />holes drilled to characterize the PR -7 Mine Expansion Area. As depicted in Permit Figure 3.5-2, this <br />surface geological material will be placed on top of the dragline spoils, and following the restoration of <br />approximate original surface contour, will be covered with topsoil. <br />The second overburden removal method used by TMI consists of dozer stripping operations in a zone <br />below the H coal seam down to the top of the L coal seam, from a depth of approximately 56 to 167 <br />feet. As shown in Figure 3.5-2, this material is pushed by dozers over the highwall and onto the bottom <br />of the previous mine pit. With this mining method, dozer spoils are mixed twice. Once as they are <br />stripped during the removal operations from a cut often hundreds of feet long, and secondly as the <br />dozer spoils fall over the previous mine highwall onto the pit floor. <br />The third overburden stripping method consists of dragline stripping, which typically handles all of the <br />materials from the bottom of the L coal seam to the top of the final coal seam to be mined. Thus, the <br />dragline will remove overburden materials from a depth of approximately 170 feet to a depth of <br />approximately 236 feet. Dragline spoil will be mixed initially during removal and secondly as it is <br />dumped from the dragline bucket into the previous mine pit. <br />The "multiple equipment scenarios" mining technique employed by TMI results in a significant amount <br />of mixing and homogenization that reduces the likelihood of marginal or unsuitable overburden or spoil <br />pockets occurring. These different mining methods result in significantly more mixing or dilution of <br />potential suspect materials than is typically associated with mining that uses a more uniform mining <br />method. <br />2-391 u <br />