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~• <br />Preliminary sampling indicated that approximately 13 transects were needed to obtain statistigl <br />sample adequacy. Calculations of minimum sample size ruing the 13 transect sample indicated that sample <br />adequary was actually reached after 3 samples (x = 56, s' = 53.06). Thus, the sample data was determined <br />to be statistically representative of the reclaimed mine site and vegetative cover sampling was discontinued. <br />Site vegetative cover has substatially increased over the values obtained during the 1985 vegetation <br />survey. The minimum cover value of 4a percent is more than double the highest 1985 value of 20 percent <br />and the maximum cover value (67 percent) is more than three times the 1985 maximum cover estimate. <br />Although, overall cover is visibly improving, there are some areas where the vegetative cover consisu mostly <br />of noxious species such as Lactucn serriola. This condition appears relatively unchanged from 1985 <br />observations. <br />Herbaceous Production <br />Total herbaceous production for the site was approximately 550 pounds per acre. Plano clipped in <br />the production quadrate were separated into five groups, based on life form (annual grass, perennial grass, <br />biennial (orb, and perennial (orb) and origin (native and introduced). Perennial native grass accounted for <br />the greatest production with approximately 280 pounds per acre. Perennial introduced grass produced almost <br />as much as the perennial native grass, 200 pounds per acre. Together, these two groups accounted for almost <br />86 percent of the annual herbaceous production on the site. The remaining yield was produced by perennial <br />introduced Corbs (70 pounds per acre), biennial introduced Corbs (9 pounds per acre), and biennial native <br />(orbs (less than 1 pound per acre). Production by species is shown in Figure 1. <br />Preliminary sampling indicated that a relatively large sample size (n = 112) was required to meet <br />statistical sample adequacy. However, satisfying that objective was unfeasible due to time constrainu. In <br />addition, published sample number guidelines suggest that attaining such a sample size is unrealistic (OSM <br />1985). Thirty-seven production quadrats were completed in the available field time. Adequacy tesu using date <br />from these 37 quadrau indicated that approximately 65 quadrau were needed to meet statistical sample <br />adequacy requiremenu. The conclusion drawn Crom these [esu was that production was too variable to meet <br />statistical adequacy tesu in a realistic number of samples and more time is needed for production to equalize <br />across the revegetated area. <br />Woody Plant Density <br />Mean shrub density was approximately 20 stems per aae. This density is considerably less than [he <br />revegetation success criterion of at least 500 stems per aae (Sun Coal Company 1986). Of the six shrub <br />species seeded on the site, only two species, Purshia rridentata and Aunus virginianus were detected. Three <br />additional species were observed on the site but not detected in sampling quadrau: Chrysothamm~us <br />nauseosus, Antelanchier alnifolin, and Rosn woodru. In addition, one species (Artemisia tridenrara) that was <br />not part of [he seed mixtures applied to the site was observed growing on site. Scattered clumps of <br />transplanted Aunus virginianus were observed but not detected during sampling. Most of the clumps <br />appeared to be marginally alive. <br />Species Diversity <br />Approximately 30 plant species were identified during the 1988 revegetation monitoring survey. <br />Table 2 lisu recorded species and indicates which were not detected on transecu or in quadrau bu[ were <br />observed on the site. Although a[tempts were made to iden[ify all species occurring on revegetated area, <br />some species may have been missed due to the time of year and desiccated nature of many planu. <br /> <br /> <br />