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Six species of the 43 encountered during cover sampling accounted for greater than <br />three percent relative cover. Of those species, four were woody. In order of decreasing <br />dominance the species were; Acer negundo (27.49%), Picea pungens (18.68%), <br />Popu/us angustifo/ia (12.28%), Poa pratensis (5.96%), Symphoricarpos rotundifolius <br />(3.91 %), and Dactylis glomerata (3.56%). Of the fort species, Solidago occidentalis <br />was the most prevalent with 2.31 percent relative cover. <br />RIPARIAN COIVIl~tUNITY SAMPLING AT THE WEST ELK MINE <br />The riparian community was sampled and described in 1976 as part of the original <br />environmental sampling effort prior to permit application submittal (MCC, 1996). The <br />1976 sampling evaluation found the riparian community limited in extent and <br />coincident within drainages within the study area. The original study noted the <br />variability of the riparian community. The riparian community was characterized by <br />the presence of Populus angustilolia and Acer negundo. Crataegus species and Saliz <br />species were noted as common along the drainages. Within the quantitatively sampled <br />riparian stand, the 1976 study noted a canopy comprised of Ater negundo and Populus <br />tremuloides. Two shrub layer were identified, a tall layer with Crataegus and Acer <br />negundo saplings, and a lower shrub layer with Amelanchr'er alnitolia and <br />Symphoricarpos rotundifolius. Poa pratensis was noted as the dominant herbaceous <br />layer component. Twenty-nine species were encountered in the riparian community <br />sampling in the original study. AIotable was the number of introduced species <br />• encountered in the riparian sampling (50% according to the narrative). <br />The 1996 quantitative sampling show very similar results to those of the 1976 <br />sampling. The 1996 sampling did not reveal Populus tremuloides as a significant <br />component of the canopy of the riparian community. However, as noted previously, <br />the riparian community intergrades significantly with the other communities in <br />Sylvester Gulch. The 1976 sampling identified one shrub stratum and a herbaceous <br />dominated low stratum, while the 1996 sampling identified these strata and added a <br />medium shrub stratum and low shrub stratum. Differences exist between the important <br />shrub species in the 1976 and 1996 studies. In 1976, Amelanchier alnilolia is noted as <br />being a significant contributor to the shrub stratum, while in 1996, it was not a notable <br />component. Total species numbers were higher in 1996 (43 versus 29), however, there <br />was only one representative sample analyzed from the riparian community in 1976. <br />Based on these comparisons of 1976 and 1996 characterizations of the riparian <br />community, it is apparent that the community has not significantly changed in cover, <br />dominant species, or composition over the twenty year period. <br /> <br />-zo- <br />