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Last modified
1/26/2010 2:16:28 PM
Creation date
10/12/2006 12:47:06 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8220.111.K
Description
Central Utah Participating Project
State
UT
Basin
Colorado Mainstem
Date
7/29/1988
Title
Final Biological Opinion: Duchesne River Basin Utah
Water Supply Pro - Doc Type
Biological Opinion
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<br />~ <br /> <br />C-J <br /> <br />("j <br />C\l <br />c:. ' <br />c: <br /> <br />20 <br /> <br />the suspended zone for discharges less than bank full. Depending on <br />the supply-capacity relationship. either deposition or scour could be <br />occurring. When the cobbles move. the sand. of course. is washed from <br />the interstices and may be completely removed from around the cobbles. <br />Rearrangement of the cobbles will result in more stability of the <br />armor layer. On the falling limb. the armor layer becomes a trap.for <br />sands until finally. the sand reservoir is again filled. Without <br />cobble movement. sand will be scoured only to a depth of one-half to <br />one median cobble diameter below the cobble bed surface." <br /> <br />In the flume experiments. the sand level was observed approximately <br />0.50 to 1 cobble diameter below the surface of the cobble bed. which compared <br />to field observations of sand depth at approximately 0.50 to 1 median cobble <br />diameter. O'Brien reported a cobble size range of 50-100 mm with a median <br />size of 75 mm at the spawning site. Milhous (1982) proposes discharges of <br />approximately 0.50 of that required to initiate cobble movement will be <br />capable of extracting sands and fines from the cobble substrate. Thus. after <br />the supply of sand diminishes. flows of sufficient magnitude and duration are <br />required to scour the cobble bed in preparation for spawning and incubation. <br /> <br />Although the location of spawning areas in the Colorado River is not well <br />defined. the presence of larvae downstream of the Walker Wildlife Area, in <br />the Lorna to Black Rocks reach and near the confluence of the Dolores River, <br />demonstrates that spawning does occur. Osmundson and Kaeding (1989 and 1991) <br />reported that water temperatures in the Colorado River were suitable for <br />spawning in the Grand Junction area. In 1986. a year of high runoff. suitable <br />temperatures for spawning (200 C) occurred in the first week of August. In <br />1989. a year of low runoff. the mean temperature reached 200 C during the last <br />week of June. Miller et al. (1982) and Archer et al. (1986) demonstrated that <br />Colorado squawfish often migrate considerable distances to spawn in the Green <br />and Yampa Rivers. and similar movement has been noted in the mainstem Colorado <br />River. <br /> <br />Miller et al. (1982) concluded from collections of larvae and young-of-year <br />below known spawning sites that downstream drift of larval Colorado squawfish <br />occurs following hatching. Extensive studies in the Yampa and upper Green <br />Rivers have demonstrated downstream distribution of young Colorado squawfish <br />from known spawning areas (Archer et al. 1986. Haynes et al. 1985). Miller <br />et al. (1982) also found that young-of-year Colorado squawfish. from late <br />summer through fall. preferred natural backwater areas of zero velocity and <br />1 ess than 1. 5- foot depth over a sil t substrate. Juvenil e Colorado squawfi sh <br />habitat preferences are similar to that of young-of-year fish. but they appear <br />
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