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Peabody does not propose to use any selected overburden materiels as topsoil substitutes <br />• or plant seedbed media. This is based on results of the soil survey end topsoil inventory <br />presented in Teb 9 end Table 19-3. Sufficient quantities of suitable quality topsoil are <br />available to restore the disturbed areas to the desired postmine land use. Following <br />mining, about 6 to 9 inches of suitable topsoil will be replaced (Table 19.3). <br />No topsoil will be replaced on those facilities which are to be retained to compliment the <br />final postmine lend use. These facilities include 3.3 acres of right-of-ways for Routt <br />County Roads 37 end 53 end U.S. Highway 40 (Exhibit 18-1 end Table 19.3). <br />Topsoil replacement depths of approximately 6 to 9 inches over final graded substratum at <br />Hayden Gulch loedaut will be beneficial to establishing a good seedbed and rooting <br />medium. This conclusion is supported by the literature, premine soil survey (Tab 9), and <br />vegetation inventories (Tab 10), as well as on-site data from Peabody's Seneca 1I end 11-Y <br />Mines. The anticipated loamy topsoil texture will likely have favorable infiltration end <br />water holding characteristics. Also, the subsoil/substratum medium immediately below the <br />topsoil will typically have desirable chemical end physical characteristics for plant <br />growth including low sodicity end salinity, moderately high saturation percentage for <br />• acceptable water holding char acteriaties, end no minor element toxicity problems (see Teb <br />9, Soil Resources). <br />Maintenance and Tes[ina Procedures <br />The density and physical characteristics of the replaced topsoil and upper <br />subsoil/substratum will be observed. Traffic areas end other compacted areas will be <br />ripped prior to topsoiling (see Tab 17, Table 17-1). Past experience at Peabody's Seneca <br />II Mine has shown that scarifying roads will correct the siBnificent compaction problems. <br />A topsoil resource quality control program will be implemented to ensure that topsoil is <br />salvaged end replaced es recommended. The optimum soil selvage depth for each soil map <br />unit will be evaluated on-site by an individual qualified to evaluate field observation <br />tests including soil color, rooting depth, coarse fragment content, horizonetion, and clay <br />content. Periodic field inspections will also be made by a soil scienti at. Soil samples <br />will be collected to correlate field procedures with laboratory det e. Topsoil recovery <br />depths will be recorded on the soil map by the soil scienti at to document the actual mean <br />• thickness of topsoil recovered. Color ph otogrephe of the soil profile and landscape will <br />9 <br />