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• surface stoniness <br />The sampling site location and number were plotted on the feld map as accurately as possible. <br />One 2-quart sample was taken to represent each natural soil horizon or contrasting layer within the <br />depth to 72 inches or bedrock, whichever was shallower <br />Samples were collected from hand-dug pits, three-i nch diameter auger holes or backhoe trenches that <br />were dug at all soil sampled sites. The sampled soil material was placed in clean, labeled, <br />polyethylene plastic or Tyvek® bags, and was kept cool and as dry as possible to limit chemical <br />changes. The upper horizons of many profiles were moist upon sampling and were air dried prior to <br />shipment to IML in Sheridan, Wyoming (1988) or Colorado State University (1996 and 1998) for <br />analysis. Each sample was split at the laboratory with one portion being used for analysis and the <br />archival portion retained for additional tests, if necessary. <br />Prime Farmland Determination <br />• The Montrose County NRCS district offce in Norwood, Colorado, was contacted fordetermination of <br />prime farmland status for the study area. In addition, onsite evaluations were made to determine <br />whether prime farmland existed. <br />Evaluation of Soils for Reclamation Potential <br />The soils and parent materials on the study area were rated for suitability based on criteria presented <br />in Table 2.04.9-2, Criteria for Evaluating Scil Suitability. These suitability criteria were approved by <br />CDMG in the scope-of-work. Recommended topsoil salvage depths were generated for each <br />sampled pedon and each component of a mapping unit. Salvage depths were determined following <br />a detailed evaluation of pH, electrical conductivity, saturation percent, soil texture, Sodium Adsorption <br />Ratio, calcium carbonate percent, and coarse fragment percent. <br />Topsoil salvage depths were based on average depths to the suspect parameter or average profile <br />(REVISED 2/00) 2.04.9-8 <br />