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initially plotted on the map within the reclaimed area. Permit map "Exhibit KK-1"illustrates the location of the transect sample start points. Sample locations were evaluated to ensure representative sampling over the entire reclamation area. Sample sites were located in the field by pacing from known landmarks. Transect orientation was determined from randomly generated numbers between 1 and 360 degrees and transects were not permitted to overlap or extend within 10 feet of revegetated area boundaries, to minimize impacts from "edge effect". Transect length was 50 feet. At 10 foot intervals along the transect, 10 point-intercept observations using the laser point frame were measured, resulting in 50 recorded hits per transect (10 observations X 5 locations). For statistical purposes, each cover transect served as a sample unit. These data were recorded and summarized by computing mean cover, relative cover (percent of total vegetation cover attributed to each species), and species composition. Species composition information was computed from vegetation cover data using a ratio of individual species cover to total live vegetation. (see Table 2) Production Live herbaceous production was collected using a harvest method. All of the current year's growth included within a 50 centimeter by 50 centimeter quadrat (quadrat area equal one- quarter of a square meter) was clipped at both ends of the cover transect. Full shrubs, succulents, noxious weeds, and cushion plants were not clipped. Production clippings were separated by life form and placed in paper bags, then weighed wet (fresh) in the field to assure sample adequacy (minus bag weight). Life form categories included perennial grasses, perennial (orbs, annual and biennial species. Field biomass adequacy calculations determined that a minimum of 35 samples was needed to achieve adequacy. Additional biomass quadrats were harvested until adequacy was achieved. Production standards are based on air-dry weight. Subsequent to the field data collection, samples were dried at 110°F for a minimum of 72 hours to a constant weight, and then re- weighed to determine dry biomass for each bag. Paper bag weight was subtracted from dry biomass calculations (see Table 3). Shrub Density Shrub density data were collected using a belt transect approach. All shrubs occurring within one meter on either side of the 50 foot cover transect line were counted on the basis of s ecies, resulting in a 328 ftZ area evaluated for each transect, or total sampled area of 4920 ft~. Stem count was recorded by species and reported as stems per acre. (see Table 2) Sample Adequacy Sample adequacy calculations were completed for vegetative cover and productivity. The following formula, accepted by the CDMG, was used for these calculations: