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Last modified
7/14/2009 5:02:33 PM
Creation date
5/22/2009 7:40:02 PM
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UCREFRP
UCREFRP Catalog Number
8170
Author
Trammell, M. A., K. D. Christopherson, C. L. Rakowski, J. C. Schmidt, K. S. Day, C. Crosby and T. E. Chart.
Title
Flaming Gorge Studies
USFW Year
1999.
USFW - Doc Type
Assessment of Colorado Pikeminnow Nursery Habitat in the Green River.
Copyright Material
NO
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1 <br />- At Mineral Bottom, a com arison of catch rates of Colorado ikeminnow in the fall and <br />P P <br />nonnative cyprinids in the summer showed a generally negative association, except for <br />1996, when catch rates for both groups were high. <br />8) Determine the usefulness of video imagery as a predictor of year class strength of Colorado <br />pikeminnow; and 9) Refane the interpretation of video so that "quality" nursery habitats can <br />be distinguished. <br />- In the 1.5 km Ouray reach, the relationship between area of habitat interpreted from the <br />videos and from the field maps was linear (rz = 0.89, p = 0.001). The area interpreted <br />from the video prints tended to slightly underestimate the area interpreted from the field <br />maps. <br /> - This analysis demonstrated that trends in total nursery habitat availability can be <br /> assessed from estimating habitat area from video, but did not assess the availability of <br /> high quality habitats. Although quality can be inferred from geomorphic setting and <br /> size of habitat, depth of habitat cannot be determined from video. <br /> - Although nursery habitats can be identified from the video imagery, it is not a useful <br />predictor of year class strength because habitat availability is not a good predictor of <br /> year class strength. <br /> - This analysis showed that the total habitat area available in 1963 at base flow was <br /> similar, but less than the area of available habitat found during the 2-year study period. <br /> The overall contribution of different geomorphic features to habitat availability has <br /> changed little since dam regulation. <br />1) Compare intensive sampling data and the concept of habitat utilization to standardized <br />monitoring data to assess a) ways of refining standardized monitoring procedures and b) <br />ways of making greater use of the data currently being collected. <br />- ISMP protocol calls for sam lin backwaters with minimum surface area of 30 m2 and <br />P g <br />minimum depth of 0.3 m. This depth is nearly identical to the mean depth (0.33 m) for <br />backwaters in which Colorado pikeminnow were collected at Ouray. The ISMP <br />minimum area is much lower than the mean for Colorado pikeminnow backwaters at <br />Ouray NWR (992 m2). However, Colorado pikeminnow were caught in backwaters as <br />small as 19 mZ. <br />1 Colorado pikeminnow were shown to prefer the type of habitats which the standardized <br />monitoring program (ISMP) specifies should be sampled, although other habitats are <br />also used. <br />- In Mineral Bottom, catch rates of the intensive sampling and catch rates of the ISMP <br />sampling were highly correlated. <br />xviii <br />fl <br />
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