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<br />-22- <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 />flows made comparisons unrealistic and caused statistical testing to <br />show non-significant differences. Stations on the Yampa River and at <br />Jensen on the Green River did not show significant differences in <br />total densities between years. <br />Species Occurrence and Distribution <br />Spatial Trends. Occurrence of individual taxa for each station <br />from 1978 through 1980 is listed in Table 7. Individual taxa den- <br />sities for each sample period from 1978 to 1980 are presented in Table <br />27 of Appendix II. Baetis spp., Simulium sp., Chironomidae, and <br />Gammarus lacustris all exhibited highest densities near the dam at <br />Little Hole (7 MBD) and Taylor Flats (16.5 MBD) (Figure 2) and were <br />the domi nant taxa present at these stat ions. Wade and Curt is (49 MBD) <br />supported many of the same taxa as Little Hole and Taylor Flats (Table <br />7). However, greater numbers of organi sms whi ch occurred sporadi ca lly <br />at the upper two stat ions such as Ephemere 11 a i nermi s, Brachycentrus <br />sp., Hydropsyche sp., and Hydroptila sp. were often observed at this <br />station. Dominant taxa at Wade and Curtis included Baetis spp., <br />Chironomidae and Brachycentrus sp. Stations on the Yampa River and <br />the lower Green River (Jensen) supported many additional taxa, pri- <br />marily Ephemeroptera and Trichoptera, not found in the Green River <br />immediately below Flaming Gorge. Dominant taxa at these stations <br />varied seasonally, dependent on the life histories of the organisms <br />involved. Baetis spp. and Chironomidae tended to dominate spring and <br />early summer samples while seasonally abundant species such as <br />Traverella albertana, Tricorythodes spp., Hydropsyche sp., and <br />