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PERMFILE57376
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PERMFILE57376
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Entry Properties
Last modified
8/24/2016 10:59:44 PM
Creation date
11/20/2007 5:25:29 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1996083A
IBM Index Class Name
Permit File
Doc Date
4/22/2004
Doc Name
After 1996
Section_Exhibit Name
Exhibit 09 Wildlife
Media Type
D
Archive
Yes
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6 • <br />of its characteristics in a laboratory flume study. O'Brien (1984) concluded that incipient motion <br />of the cobble bed is required to clzan cobbles for spawning and estimated that this takes <br />dischazges of about 21.00 cfs. However. Harvey et al.(1993) concluded that since flows <br />required for incipient motion of bed material are raze (20 } eaz return period event) and spawT~ing <br />occurs annually, another process must be cleaning the cobbles. Their study found that in Yarnpa <br />Canyon recessional flows routinely dissect gravel bars and thereby produce tertiary bazs of clean <br />cobble at the base of the riffles. These tertiary bars aze used by Colorado pikemittnow for <br />spawning. Harvey et al. (1993) recognizes the importance of high magnitude, low frequency <br />dischazges for the formation and maintenance of midchannel bars. Dissection of bars without <br />redeposition by high magnitude flows would lead to conditions where spawning habitat is no <br />longer available (Harvey et al. 1993). <br />It is unknown whether tertiary bazs used for Colorado pikeminnow spawning in Yampa Canyon <br />are available in the 15-mile reach of the Colorado River. There, significant motion of bed <br />material occurs at neaz bankfull discharge of 22,000 cfs (Van Steeter 1996). These flows occur <br />on average once in 4 yeazs. Van Steeter (1996) concludes that flows of this magnitude are <br />important because they generally remove fine sediment from the gravel matrix which maintains <br />the invertebrate community and cleans spawning substrate. <br />Although the location of spawning areas in the Colorado River is not well defined, the presence • <br />of larvae downstream of the Walker Wildlife Area, in the Loma to Black Rocks reach and near <br />the confluence of the Dolores River, demonstrates that spawning does occur. Osmundson and . <br />Kaeding (1989 and 1991) reported that water temperatures in the Colorado River were suitable <br />for spawning in the Grand Junction area. In 1986, a year of high runoff, suitable temperatures for <br />spawning (20° C) occurred in the first week of August. In 1989, a year of low runoff, the mean <br />temperature reached 20° C during the last week of June. Miller et al. (1982) and Archer et al. <br />(1986) demonstrated that Colorado pikeminnow often migrate considerable distances to spawn in <br />the Green and Yampa Rivers, and similaz movement has been noted in the main stem Colorado <br />River. <br />Miller et al. (1982) concluded from collections of larvae and young-of--year below known <br />spawning sites that there is a downstream drift of larval Colorado pikeminnow following <br />hatching: Extensive studies in the Yampa and upper Green Rivers have demonstrated <br />downstream distribution of young Colorado pikeminnow from known spawning azeas (Archer et <br />al. 1986; Haynes et al. 1985). Miller et al. (1982) also found that young-of--year Colorado <br />pikeminnow, from late summer through fall, preferred natural backwater azeas of zero velocity <br />and less than 1.5-foot depth over a silt substrate. Juvenile Colorado pikeminnow habitat <br />preferences aze similar to that of young-of-yeaz fish, but they appear to be mobile and more <br />tolerant of lotic conditions away from the sheltered backwater environment. <br />Information on radio-tagged adult Colorado pikeminnow during fall suggests that fish seek out <br />deepwater areas in the Colorado River (Miller et al. 1982), as do many other riverine species. • <br />
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