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areas. These measures provide a means of examining progress toward the return of diverse <br />• species composition in the reclaimed areas. <br />Plant Species Listing <br />Scientific names used follow Weber and Wittman (1996); common names cited are found in <br />Beetle (1970), Nickerson et al. (1976), or Soil Conservation Service (1979). Cross-references <br />between older names and the revised scientific nomenclature for the flora of Western Colorado <br />used here can be made by reference to Appendix 2 of this report. <br />During the course of the fieldwork, a list of all plant species encountered (quantitative plus <br />incidental observations) was compiled for each reclamation area and the three reference areas. <br />These lists are summarized in Appendix 2, Species Presence for All Areas, which includes <br />current nomenclature and cross references to older nomenclature. Note that all big sagebrush <br />plants encountered were referred to as Seriphidium tridentatum. <br />Photographic Record <br />Within each reclamation and reference area, representative color photographs were taken to <br />document the appearance of the vegetation in 2003 (Appendix 4). Within each reclaimed area <br />• photograph, a placard identifies the particular area and sample. <br />Statistical Methods <br />Sampling was conducted at randomly located sites. Each reclamation antl reference unit <br />identified in the SCC Scope of Work was gridded and numbered. Grid cell size was 100 ft x 100 ft <br />in reclaimed areas, and 50 ft x 50 ft in reference areas. These grid cells were placed <br />contiguously on maps of 1:4800 scale. Sample locations were selected from the numbered grid <br />cells. The SCC-assigned numbers of samples for a given parameter in a given area reflected <br />previously experienced sample variability or the level of precision required in a given area. <br />Random numbers generated by computer were used to select grid cells, in the middle of which a <br />sample point was placed, and recorded on the field maps. These sample points were located as <br />accurately as possible in the field using aerial and topographic maps and pacing from known <br />locations. Cover and woody plant density transects were located and oriented using a blind throw <br />of a meter stick. Final location of each herbaceous production quadrat was accomplished with a <br />blind throw of the sampling hoop made from the origin of the associated coverlwoody plant <br />density transect. At each coverlwoody plant density sampling location, the slope, expressed as a <br />percent, and aspect of the site, in degrees not corrected for magnetic declination, were <br />determined and recorded, as was the orientation of the transect. <br /> <br />