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6 <br />3 RESULTS <br />3.1 VEGETATION OF RIPARIAN ZONES <br />The width and height of the riparian zone as measured in different reaches of the <br />Green River is presented in Table 1. No clear difference between canyon and park areas was <br />detected from these data. The riparian zone was narrowest in Red Canyon just below <br />Flaming Gorge Dam, but on average was widest in Lodore Canyon. The upper boundary of <br />the riparian zone was lowest in Browns Park, but relatively high in Island and Rainbow <br />Parks. <br />Fifty-four plant species were identified at 2,165 sampling points along the transects; <br />an additional 14 taxa were identified to genus or family (plant nomenclature follows Goodrich <br />and Neese 1986). The relative abundance of species and taxa is presented in Table 2. <br />Grasses, which were recorded at 44% of all sampling points, were the most common of all <br />taxa recorded but were not identified to species. Other common species in the river corridor <br />included scouring rush (19%), juncus (14%), western goldenrod (12%), common spikerush <br />(11%), box elder (11%), carex (9%), tamarisk (7%), field horsetail (M), and coyote willow (7%). <br />(See the appendix, Table A.4, for the scientific names and wetland indicator status [Reed <br />19881 of all species observed.) <br />For most species, abundance varied considerably among reaches, especially between <br />canyon and park reaches (Table 2). Species most common in canyons included box elder <br />(especially Lodore Canyon), western goldenrod, and scouring rush. Species more common in <br />the parks than in the canyons included common spikerush, coyote willow, and Fremont <br />cottonwood. <br />Both distance from and elevation above the river were important determinants of <br />species abundance (Tables 3 and 4). Presumably these factors were important insofar as they <br />determined soil moisture, and species-specific requirements for moisture and flood tolerance <br />determined where those species occurred on the distance/elevation gradient. This interpre- <br />tation is supported by the observed position of each species along the elevation gradient and <br />their wetland indicator status (see Table AA) - obligate wetland species (i.e., species that <br />occur almost always in wetlands) were found closer to the river, whereas facultative wetland <br />species (i.e., wetland species sometimes found in uplands) or nonwetland species were found <br />farther from the river. <br />As might be expected, elevation appeared to have a stronger influence than distance <br />on species occurrence because of the effect of elevation on depth to the water table. Some <br />woody riparian species (e.g., box elder and rabbitbrush) increased in abundance with <br />increasing distance and elevation; others (e.g., coyote willow and tamarisk) appeared to <br />occupy a specific elevation midway between the lower and upper boundaries of the riparian <br />zone. Wetland species decreased in abundance with distance and elevation (e.g., cattail, <br />common spikerush, and coyote willow) or were more prevalent at a particular elevation or