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Last modified
1/26/2010 3:16:29 PM
Creation date
10/12/2006 4:47:35 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8240.200.48.D.3
Description
Wolford Mountain
State
CO
Basin
Colorado Mainstem
Water Division
5
Date
3/12/1998
Title
Wolford Mountain Biological Opinion and attached MOU
Water Supply Pro - Doc Type
Biological Opinion
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<br />28 <br /> <br />reduces the value of these habitats for endangered fishes. Furthermore. <br />higher flows are required to flush sediments from vegetated backwaters than <br />from unvegetated ones. Qsmundson and Kaeding (1991) reported observations <br />that. on the 15-mile reach during the drought years of 1988 to 1990. <br />backwaters were filling in with silt and spring flows were not sufficient to <br />flush out the fine sediment. Also. they reported that tamarisk colonized sand <br />and cobble bars. The lower frequency of high water years, therefore. <br />decreases the frequency at which silt and sand is flushed from backwaters. <br />fine sediments are flushed from gravel/cobble substrates. and vegetation is <br />scoured from backwaters and bars. As a result. the frequency 'at which these <br />habitats are suitable for use by endangered fishes has decreased. <br /> <br />Seasonal Habitat Availability <br /> <br />Summer (August-Qctober): Qsmundson et al. (1995) reported that availability <br />of habitats did not differ significantly between periods of moderate flows and <br />low flows. Though absolute area of habitat decreases with declining flows, <br />relative area or percent composition of habitat types changes little. <br />However. squawfish habitat use patterns did change. The fish used a greater <br />variety of habitats during moderate flows than during low flows, During <br />moderate flows. the fish used primarily backwaters, eddies. and pools. During <br />low flows. the fish used slow and fast runs almost exclusively, The change in <br />habitat use without a corresponding change in relative habitat availability <br />indicates that other factors also influence habitat selection. These factors <br />could include changes in quality of physical habitat features such as <br />diversity, depth. dissolved oxygen. etc., or changes in biotic interactions. <br />Qsmundson et al. (1995) interpreted the squawfish behavioral changes as <br />reflective of suboptimal conditions; the behavioral changes demonstrate the <br />ability of the species to modify their habitat use patterns to temporarily <br />cope with adverse conditions and do not demonstrate habitat preferences under <br />optimum conditions. Qsmundson et al. (1995). therefore. based their flow <br />recommendations on the habitat-selection behavior of adult squawfish observed <br />during the higher somewhat more natural flow conditions. <br /> <br />Winter (November-March): Qsmundson et al. (1995) reported that flows during <br />the winter are usually moderate because no water is diverted for irrigation <br />and because additional water is released through upstream dams to increase <br />reservoir storage capacity in anticipation of spring runoff. The relative <br />availability of slow runs and riffles during the winter was very similar to <br />their availability during summer. As in the summer. backwaters, eddies, and <br />pools were the preferred types of habitat in the winter. However. whereas <br />eddies were most preferred in summer, pools were most preferred in winter. <br />Adult squawfish used fewer habitat types overall during winter than during <br />
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