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remaining species have shown an increase in individuals over time. This is not <br />unexpected, as these species are more adapted to an open environment, in association <br />with graminoid species. Artemesia tridentata, Chrysothamnus nauseous, and Guterrezia <br />sarothrae are also opportunistic pioneer species in successionally young vegetation <br />communities. <br />5.3.4 HRSA Species Composition: 1996-2010 <br />Total species numbers correlated with "pre-growing season" precipitation in a directly <br />proportional relationship since sampling at the historic record vegetation community <br />began. Species number increased from the dry 1996 to the mesic 1997 and decreased <br />from the more mesic 1997 to the drier 1998 (Table 7.). In 2010, species numbers were <br />above average when compared to historic record vegetation community sampling in the <br />1990's, and higher than a direct correlation with pre-growing season precipitation would <br />suggest. <br />One new species, Balsamorhiza sagitta (balsamroot) was encountered since the last <br />historic record vegetation community sampling in 1998. This species is a native cool <br />season perennial forb found commonly in adjacent oakbrush and mountain shrub <br />vegetation communities. <br />The species numbers from the historic record vegetation community sampling indicate <br />that the composition of the community is very stable, as there have been no significant <br />increases or decreases in species numbers over the years, nor have there been significant <br />changes in the representation of the dominant species or physiognomy of the community <br />since sampling began in 1996. <br />5.4 COMPARATIVE VEGETATION COMMUNITY SAMPLING AT THE WEST <br />ELK MINE <br />The historic record vegetation community was selected because of a close resemblance <br />(location, elevation, aspect, soils, and vegetation community structure) to the dry meadow <br />herbaceous vegetation community present within the West Elk Mine permit area (Savage <br />and Savage, 1996, 1997, 1998). The dry meadow community was sampled in 1982 and <br />the dry meadow reference area was sampled in 1982 and 1995 (MCC, 1997, Savage and <br />Savage, 1995). While the dry meadow community (either affected area or reference area) <br />is no longer being quantitatively sampled, it is productive to compare observations made <br />at the historic record vegetation community to those from the dry meadow community <br />within Sylvester Gulch. Tables 7 and 8 provide comparisons of the sampled parameters <br />for the dry meadow community, dry meadow reference area, and the historic record <br />vegetation community from the years 1982 through 2010. <br />Relative cover in the dry meadow affected area, dry meadow reference area, and historic <br />record vegetation community during the sample years 1982, 1995, 1996, 1997, 1998, and <br />2010 illustrates dominance by one cool season grass species in each of the communities <br />(Table 8). In the 1982 dry meadow community, the species was Agropyron smithii. In <br />the dry meadow reference area and the historic record vegetation community, the species <br />Mountain Coal Company, LLC Page 10 <br />Historic Record Study Area Vegetation Sampling Report: 2010