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• Using the NRCS data, eight soil types were identified within the MLE study area <br />(Grenadier-like-Unnamed soils, Quander-Varden Complex, Rogert soils, Ess-Bushvalley, <br />Ivywild-Catamount, and Seitz). The Rogert soil type was further divided into three sub- <br />units. Most of the soil units mapped in previous soil surveys remain valid; however the <br />NRCS has revised soil units and descriptions. <br />The 1997 JBR survey identified and mapped hydric soils in the MLE study area. A <br />review of the most current NRCS soil unit maps indicates that the hydric soils correspond <br />closely to soil unit CQ (Adderton-Cryaquolls). Areas that were historically mined or <br />otherwise altered by human activity were identified as disturbed soils. All of the mapped <br />soil units are shown on Figure 2-1 of Appendix 3 in Volume III of this document. <br />All soils in the area are characteristic of well drained mountain soil complexes found on <br />steep slopes and exhibiting low water capacity, rapid surface water runoff, and a <br />susceptibility to water erosion. The soils are differentiated based on slope and aspect and <br />support different vegetation types. Each of these soils is described in detail, including the <br />thickness of the soil horizon for each type and the suitability of each type for use in <br />reclamation, in Appendix 3 in Volume III of this document. <br />• Range carrying capacities have been determined to be an average value of 3.1 acres per <br />Animal Unit Month ("AUM") for the Quander-Varden complex, 3.8 acres per AUM for <br />the Rogert soil, and 1.3 acres per AUM for the hydric soils. <br />Most of the soil groups presented above are suitable for use in reclamation. As part of the <br />ongoing mining operations at the Cresson Project, CC&V salvages soil that is suitable for <br />assisting with revegetation in accordance with its reclamation objectives of revegetation <br />on suitable slopes (see Reclamation and Closure, Section 11.0 of this Project <br />Description). Note that the soil depth information presented in Table 2-2 of Appendix 3 is <br />not strictly indicative of soil depths that can be salvaged. The actual depths are functions <br />of slope, surface rock, aerial extent, vegetative cover, and historical mining. Soil depths <br />vary greatly depending upon their position on the terrain, with the shallowest soil on the <br />upper slopes and deepest at the toe of the slope. The presence of rock outcrops in some <br />areas renders salvage operations impossible. By removing large roots, stumps, and <br />pushing slash, unavoidable mixing of the thin topsoil with the rocky subsoils occurs, <br />producing a material potentially not well suited for salvage as soil. The depth that can be <br />recovered also is a function of the nature of the soil and weathered bedrock, and the <br />capabilities of the dozers and other mechanized salvage equipment. As discussed in <br />• Cripple Creek & Victor Gold Mining Company <br />Cresson Project Mine Life Extension <br />4-18