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material (identified to genus and species), litter, rock, or bare ground. Shrubs, if encountered, were not counted as a component of the herbaceous cover data. A 1:1200 scale (1 inch=100 ft.) map of the permit area (permit map "Exhibit KK-1") was used to delineate the sampling area consisting of all reclaimed areas within the permit area. A Cartesian grid was overlaid upon the reclaimed areas and sample sites were established using a randomization computer program. Computer-generated random numbers were used to establish a pool of (x,y) coordinates. Twenty-two random locations for transect starting points were 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 reclaimed 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) Transect 8 was eliminated due to a large portion of the transect falling within ten feet of the reclaimed area boundary. 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 to 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 60 samples was needed to achieve adequacy. A sample size of 30 was obtained for production, which allowed for a statistically valid demonstration that reclaimed area production exceeded 90% of the standard, at the 90% level of statistical confidence. Success was demonstrated by use of the "reverse null" one-sample t-test. Production standards are based on air-dry weight. Subsequent to the field data collection, samples were oven 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 Densit There is no reclamation success standard for shrub density at this site Shrub density data was not collected. Shrub data was collected in 2002 and 2003 sampling efforts.