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r <br />. ~ P g"Za <br />ass/~ <br />~v°° ~ ,~ <br />` 29 <br />Habitat Depth <br />The biological assessment includes results of an analysis of effects on <br />habitat depths caused by the Project's re ction of flows (Biological <br />Assessment, Appendix 6, Tables 3.14 throw h 3.19 and Attachment G). This <br />analysis was based on extrapolation of fl w/depth measurements taken in four <br />study sites within the 15-mile reach as d scribed in Osmundson et al. (1995). <br />The results show that reductions a itat the for all habitat types in <br />the 15-mile reach would range f om 0 to 1 inch on average, during both-the <br />summer and winter. The results i-fin i~ a at effects on habitat depth are ~''~"'~-- <br />significant only during the summer (August through October) with most effects <br />associated with backwater habitats. ~. <br />Habitat Area 1, ~•~~~ <br />'~~:, . s a <br />The biological assessment also includes the results of an analysis of changes ~,,~~ <br />in habitat areas caused by the Project's reduction of flows (Biological <br />Assessment, Appendix B, Tables 3.20 and 3.21). This analysis was based on ~ ~ ~'' <br />extrapolation of flow/area measurements taken in four study sites within the P ~"ZO <br />15-mile reach as described in Osmundson et al. (1995). Changes to habitat ~~ ~ <br />areas were calculated in two ways. The calculations were first performed 6~c~(> <br />assuming that the four study sites contain 66.8 percent of the total habitat h. " <br />in the 15-mile reach; this assumption was based on the Service's finding that ~~ <br />66.8 percent of radio telemetered squawfish locations in the 15-mile reach <br />occurred within the four study sites. These results show that the area of all <br />habitat types would decrease in the 15-mile reach by 0.36 acre in the summer <br />and 0.25 acre in the winter from a total of 84 acres and 96 acres <br />respectively, and the area of preferred habitats would increase in the 15-mile <br />reach by 0.02 acre in the summer and 0.40 acre in the winter from a total of <br />5.1 and 10.7 acres respectively. The calcul m <br />assumin a linear relationship between a itat area in the four study sites <br />n - ch. T e u s s ow a the area of al a itat types <br />would decrease in the 15-mile reach by 1.2 acres in the summer and 1.1 acres ~_>~ <br />in the winter from a total of 396 acres and 456 acres respectively, and the ~--~ 7 <br />area of preferred habitats would increase in the 15-mile reach by 0.07 acres <br />in the summer and 1.9 acres in the winter from a total of 24.3 acres and <br />50.8 acres respectively. ~ _ 5~Q ~,c ~~s~ <br />r3 A z <br />The analysis of changes in area of preferre s during summer as <br />presented in the biological assessment is law The analysis evaluated the <br />effects on habitat areas caused by the Pro~ec s reduction of flows from <br />814 cfs to 795 cfs. However, backwaters, eddies, and pools were mistakenly <br />identified as the preferred habitats at these flows. Slow and fast runs are JG`,~ ~ <br />the preferred habitats at these flows. According to the results of the <br />analysis, the Project will decrease the area of slow and fast runs. <br />Also, the extrapolation of measurements of habitat area in the four study ~: <br />sites to the entire 15-mile reach assuming that the four study sites contain ~~~~'`~ x <br />66.8 percent of the total habitat area in the 15-mile reach (basemen t ems' `'"'~'~ <br />Service's finding that 66.8 percent of squawfish radiot ons in <br />the 15-mile reach occurred within the four study site s flawed. is not <br />possible for the four study sites, which constitute 14 a length <br />