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GENERAL31841
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Last modified
8/24/2016 7:54:44 PM
Creation date
11/23/2007 7:06:42 AM
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Template:
DRMS Permit Index
Permit No
M1999002
IBM Index Class Name
General Documents
Doc Date
7/22/1999
Doc Name
FINAL ENVIRONMENTAL IMPACT STATEMENT VOLUME 2 APPENDIX L
Media Type
D
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30 <br />primarily backwaters, eddies, and pools. During low flows, the fish <br />used slow and fast runs almost exclusively. The change in habitat use <br />without a corresponding change in relative habitat availability <br />indicates that other factors also influence habitat selection. These <br />factors could include changes in quality of physical habitat features <br />such as diversity, depth, dissolved oxygen, etc., or changes in biotic <br />interactions. Osmundson et al. (1995) interpreted the behavioral <br />changes as reflective of suboptimal conditions; the behavioral changes <br />demonstrate the ability of the species to modify their habitat use <br />patterns to temporarily cope with adverse conditions and do not <br />demonstrate habitat preferences under optimum conditions. Osmundson <br />et al. (1995), therefore, based their flow recommendations on the <br />habitat-selection behavior of adult observed during the higher <br />somewhat more natural flow conditions. <br />Winter (November-March): Osmundson et al. (1995) reported that flows <br />during the winter are usually moderate because no water is diverted <br />for irrigation and because additional water is released through <br />upstream dams to increase reservoir storage capacity in anticipation <br />of spring runoff. The relative availability of slow runs and riffles <br />during the winter was very similar to their availability during <br />summer. As in the summer, backwaters, eddies, and pools were the <br />preferred types of habitat in the winter. However, whereas eddies <br />were most preferred in summer, pools were most preferred in winter. <br />Adult used fewer habitat types overall during winter than during <br />summer. Although fast runs and riffles were used during the summer, <br />they were not used during the winter. The colder water temperatures <br />in winter which cause lower metabolic rates may account for the <br />avoidance of high velocity sites. Absolute area of pools increases as <br />flows decrease and slow runs lose velocity. Because Osmundson et al. <br />(1995) did not sample low flows in the winter, they could not <br />determine if pools would still be preferred in the winter at lower <br />flows. Therefore, they recommended winter flows at the moderate flow <br />level which maximized weighted area of preferred habitats. <br />Spring (April-July): Osmundson and Kaeding (1989) reported that use <br />of low velocity habitats such as backwaters and flooded gravel pits is <br />greatest during the spring runoff. It is believed that use these <br />habitats during the runoff to escape the high velocity, low <br />temperature flows of the main channel. Because backwaters, flooded <br />gravel pits, and other low velocity habitats are considerably warmer <br />than the main channel during the runoff, these habitats allow to <br />extend their growing season substantially. The earlier warming of <br />these habitats may also be important in enabling to reach spawning <br />condition by the time flow and temperature in the main channel are <br />optimum for spawning. Osmundson et al. (1995) reported that the <br />numbers of backwaters and flooded gravel pits increases with <br />increasing spring flows. (Although the number of backwaters <br />eventually decreases as increasing flows convert backwaters to <br />aidechannels, the number of other low velocity habitats likely <br />
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