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<br />-28- <br /> <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 />Cheumatopsyche sp. dominated summer and fall samples. Table 26, <br />Appendix II, lists many species found in this study and whether they <br />were most common in the regulated (Little Hole, Taylor Flats, and Wade <br />and Curtis) or unregulated (Lily Park, Boxelder Park, and Jensen) par.... <br />tions of the Green and Yampa rivers. <br />Annual Trends. Little Hole and Taylor Flats exhibited differences <br />in abundance of certa in taxa between 1978 and 1980. Peak dens i ties of <br />Hydroptila sp. increased from 0 at Little Hole and Taylor Fld.ts in <br />1978 to 724/m2 and 886/m2, respectively, in 1980. Gammarus lacustris <br />exhibited peak abundances at Little Hole increasing from 452/m2 in <br />1978 to 3225/m2 in 1979 to 3992/m2 in 1980. Taylor Flats also had <br />increased peak populations of this species which ranged from 0/m2 in <br />1978 to 617/m2 in 1980. Yampa River stations showed no comparable <br />increase of these taxa during the same time period. Other taxa which <br />exhibited slight to moderate increases in abundance at these two sta- <br />t ions i nc 1 uded Ephemere 11 a i nermi s, Mal enka sp. , Hydropsyche, and <br />Planaria. Annual changes in abundance of individual taxa at Wade and <br />Curtis were difficult to assess due to the small numbers involved and <br />the large variation present. <br />Species Diversity <br />Spatial Trends. Shannon-Weaver species diversity values calcu- <br />lated for each sample period from 1978-1980 are presented in Table 8. <br />Figure 3 shows mean yearly diversity values for each station on the <br />Green River from 1978-1980. <br />