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Five sub-types of the Bottomland community were identified (Wetland, Mountain Shrub, Sagebrush, <br />Riparian Bottom, and Grassland) during mapping and field verification and are described below. Owing <br />to its disproportionate importance as a habitat, as well as jurisdiction by the U.S. Army Corps of <br />Engineers under the Clean Water Act, the wetland subtype is fully described in Section 3.7.4. as a <br />paraphrased section from the Wetland Delineation submitted to the Corps. The mountain shrub subtype <br />is simply described as invasions from upland sites into the numerous concave basins of the various <br />headwater drainages throughout the study area. These invaded areas exhibit an identical character and <br />ecological attributes as is described for the larger community presented under Section 3.5. The <br />sagebrush and grassland sub-types generally occupy the relatively flat floodplain terraces extending from <br />the toe of the adjacent slopes to the creek channel or wetland. If recent burning or sagebrush removal <br />has occurred, the area has been designated as grassland. These areas are variably dominated by <br />perennial wheatgrass species (Agropyron sp.), Great Basin wildrye (Eiymus cinereus) (at higher <br />elevations), or annual bromes with occasional sagebrush or rabbitbrush reinvasion. The grasslands in <br />the Bottomland community differ from upland Grassland communities in that they exhibit substantially <br />higher production and cover values due to the increase soil moisture levels. The sagebrush sub-type is <br />visually dominated by basin big sagebrush with lower densities of rubber rabbitbrush, mountain <br />snowberry and silver sage. The recent drought along with channel "down-cutting" has reduced the <br />alluvial water table which appears to have contributed to a substantial die-off of basin big sagebrush on <br />the terraces, most notably in the Wilson Creek drainage. The riparian bottomland sub-type is highly <br />variable and scattered and includes the linear channel banks adjacent to the streamside and expanded <br />streamside wetlands where an overstory of boxelder (Acernegundo) is often evident. <br />3.2.2 Bottomland Reference Area <br />. The Bottomland reference area is located along Wilson Creek just external to the northeast portion <br />of the study area (see Map V1). This area was selected as a reference area because of its easy access, <br />low probability of future disturbance, and it represents a mix of sagebrush and grassland sub-types <br />within its boundaries (no areas could be located that also included the riparian bottom subtype owing to <br />its more scarce distribution). Review of Table V4 and Chart V1 indicates that the average vegetation <br />cover of the Bottomland reference area was 64.2%. Litter and rock provided an average of 31.7% and <br />0.5% of the ground cover, respectively, while bare ground exposure averaged 3.7%. The dominant <br />plant species were cheatgrass, western wheatgrass, Sandberg bluegrass (Poa secunda), basin wildrye <br />(Eiymus cinereus), and thickspike wheatgrass with 27.3%, 9.6%, 7.5%, 4.6%, and 3.2% of the ground <br />cover, respectively. Perennial plants (excluding noxious weeds) contributed 56% of the total plant cover <br />(35.8% average cover) while annual species and noxious weeds contributed 44% and 0.0% of the <br />composition, respectively. Perusal of Table V10 indicates that a total of 4 perennial species contributed <br />CEDAR (CIR2IEIEKA ?FUMS,INC. Page 17 2005 Collom Vegetation Survey