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datum for purposes of statistical analysis. Absolute and relative plant cover, species diversity, and plant life forms were determined based upon the observations collected in sampling the plarrt cover. As outlined in the Trapper Mine Permit and the Division's Guidelines, annual and biennial plant cover in excess often percent of the total vegetative cover was excluded from the calculations of "allowable cover." As directed by Trapper, litter in excess of the acceptable standard, cryptograms and rock were excluded in calculating the values of "allowable cover." The Trapper reclaimed rangelands cover success standard is based on "allowable cover." For Range Site A, which includes Rangeland Reclamation Block AD&H-A/B, the "allowable cover" standard is 52 % with at least 33 % of the rover coming from herbaceous vegetation. For Range Site C, which includes Rangeland Reclamation Block AC&D-C, the "allowable cover" standard is 47 % with at least 25 % of the cover coming from herbaceous vegetation. The "allowable cover" standard at Trapper includes perennial plant cover (minus the cover from noxious perennial weeds), and up to 10% relative affiual plant cover, and litter cover up to the maximum allowed per Range Site (Range Site A =19%; Range Site C = 22%). The Cropland Reclamation Block has no cover success standard. Production. For the two Rangeland Reclamation Blocks and the Cropland Reclamation Block, sampled using the simple random statistical sampling approach, all of the production iransect locations were randomly located within the appropriate reclamation block and along each transect a total of three randomly located one half square meter clip plots were clipped. The three plots were clipped by life forms for perennial grasses and perennial forts. As recommended in the Division's Guidelines, annuals and biennials and shrub production was not clipped. The three clip plots were then averaged into a single transect datum for purposes of statistical analysis. For each rechimation block sampled a m;n;mum of 30 production transects were used for sample adequacy calculations. Following clipping the clipped materials were dried in a drying oven in the Trapper Mine Coal Laboratory at 30 degrees C for a period of 48 hours. The revegetation production success standards are the Reference Area value for the Cropland Reclamation Block and 62.39 grams per square meter (g/m~ for the Range Site A (Rangeland Reclamation Block ADBcH-AB and 47.46 grams per square meter (g/m~for Range Site C (Rangeland Reclamation Block AC&D-C). Shrub Density. Starting at each of the 30 transect locations described above for the production sampling of Rangeland Reclamation Block AD&H-AB, the fifty-meter tape was laid out along a predetermined and randomly selected alignment. Woody stem density was determined using the center of the tape as a modified belt transect. The right-hand side of the transect was called Side A and the left-hand side of the tape was called Side B. Data collected from each side were added into a iransect value which represents the number of shrubs sampled in the 100 square meter sample plot. These data are reported in the Results Section as to the number of shrubs per 100 square meters as well as the number of shrobs per acre as outlined in the Pemut. In addition, shrub survivaVdensity counts were taken on three Shrub Clumps, constructed within