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Surface Water Effects <br />McClane Canyon is an ephemeral drainage which is normally dry. Flows that do occur <br />are in response to snowmelt or intense rainstorms, and are usually of short duration. <br />McClane Canyon drainage is tributary to East Salt Creek, which is an intermittent <br />tributary pf the Colorado River. Water quality is typical of arid climate, ephemeral and <br />intermittent systems located in marine deposited sedimentary land forms. Dissolved <br />constituents often reach very high levels following dry periods and during the winter, <br />when stream flows are made up almost entirely of recharge from ground water and from <br />stagnant or semi-stagnant pools. Suspended solids levels are high during spring runoff <br />and following high intensity rainstorms, due to sparse vegetation and erodible soils. <br />Due to the limited areal extent of surface disturbance, existence of effective sediment <br />control measures, and small quantity and acceptable quality of projected minewater <br />discharge, operations at McClane Canyon have had little effect on the quality of water <br />in McClane Canyon drainage or East Salt Creek, and no significant effects are expected. <br />Following the conclusion of mining, all culverts and diversions will be removed, and <br />a network of ephemeral drainages in geomorphic balance with adjacent areas will be <br />reconstructed on the disturbed area. Following successful vegetation establishment it <br />is expected that surface water hydrologic characteristics of the reclaimed area will <br />approximate pre-mining conditions. <br />III. TOPSOIL. <br />Soils resource information, including soil series descriptions, and evaluation of mine <br />bench materials for use as plant growth medium is provided in Section 4.4 of the permit <br />application. Information on topsoil management is provided in Sections 2.3 and 3.2, <br />and information on topsoil replacement is provided in Section 3.3. <br />No topsoil was stripped prior to mine bench and haul road construction, as this <br />disturbance occurred prior to the enactment of the Surface Mining Control and <br />Reclamatipn Act (SMCRA). Topsoil was salvaged from subsequently disturbed areas <br />including the sediment pond, riprap stockpile, and office facility areas, and, with the <br />exception of one small area addressed below, will be salvaged from approved <br />disturbance areas where construction has not yet been initiated. <br />Figure 2.2-2 (Surface Facilities Map), shows site specific mapping of soils at an Order <br />1 or II level of intensity. The mapping indicates that soils in the vicinity of the sediment <br />pond and riprap stockpile were Rivra Gravelly Sandy Loam Variant, and Nihill Loam, <br />and office facility soils were Glendive Sandy loam. Soils to be affected by the <br />proposed McClane to Munger haul road are mapped as Glendive Sandy Loam, and a <br />small area of Rivra Gravelly Sandy Loam. A small area to be affected by the proposed <br />realignment of the access road segment at the junction with the state highway is mapped <br />as Havre Loam, saline phase. <br />21 <br />