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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />bigmouth shiner ranged in relative abundance from 1.5 to 6.5 percent. All of these species were <br />found at over 50 percent of the sampling sites with the exceptions of big mouth shiners and <br />mosquitofish. Black crappies, longnose suckers, yellow perch, and green sunfish followed in <br />abundance (roughly 0.5% each of the total sample). It is interesting to note that their frequency <br />of occurrence among the sites (21-57%) was much higher than their relative abundance (0.48- <br />0.78%). Creek chub, johnny darter, brook stickleback, Iowa darter, white crappie, channel catfish <br />and bluegill were all found in small numbers. Over 14 percent of the fish sampled were <br />introduced species, while less than 3 percent were either uncommon or sensitive native species. <br />Overall, species composition and relative abundance suggest a degraded habitat. <br /> <br />The furthest downstream reach of the mainstem river in this hydrounit flows from the <br />confluence with the Big Thompson River near Greeley to a point near Fort Morgan. Seven sites <br />were sampled a total of nine times (Table 8). Again, only three species, fathead minnow, plains <br />killifish, and white sucker, comprised over 78 percent of the total sample (Table 9). By adding <br />creek chub and sand shiner, the percentage of this total reaches 92 percent. However, this species <br />composition is somewhat different from that observed in the upstream section. Sampling <br />conditions were very difficult in this reach and considered to be worse than conditions found in <br />the Henderson to Greeley reach. Red shiner, bigmouth shiner, and carp were the only other <br />common species seen (1.5-3% of the total). Brook stickleback, longnose sucker, green sunfish, <br />johnny darter, largemouth bass, white crappie, and hybrid striped bass were found in trace <br />numbers, and at only one site each. <br /> <br />The sampling crews failed to locate any water in any of the stream courses in the eastern <br />plains tributary portion of this hydrounit (Table 10). The tributaries which drain this portion when <br />water is present are Horse Creek, Lost Creek, Box Elder Creek, Sanborn Draw, Greasewood <br />Draw, and Long Draw. Although they did not document all dry locations, the sampling crew <br />reported searching the area extensively and locating no water. This area was sampled in 1988 and <br />provided much of the same results with three exceptions. One site on Boxelder Creek was found <br />to contain plains killifish, fathead minnows, Iowa darters, green sunfish, and carp, in that order of <br />abundance. Another site downstream of Horse Creek Reservoir which was dry in 1994, <br />contained water in 1988, and supported Iowa darters and plains killifish. Finally, a small reach of <br />Lost Creek contained abundant fathead minnows in 1988. <br /> <br />The obvious limiting factor in the eastern plains tributaries is lack of permanent water. <br />Analysis offish distribution in 1988 noted limited distribution offish species throughout eastern <br />plains tributaries to the South Platte River (Kehmeier and VanBuren 1990, unpublished). They <br />felt the single overriding variable was water availability. Obviously, the available habitat had <br />decreased in 1994 from what little there was in 1988. However, the extremely wet spring of 1995 <br />may have led to re-colonization of some of these dry stream courses. The potential for <br />management through habitat manipulation (pool deepening and water manipulation) and artificial <br />re-colonization is high throughout the eastern plains. <br /> <br />17 <br />