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Last modified
1/26/2010 2:18:37 PM
Creation date
10/12/2006 1:04:51 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8200.766
Description
Gunnison River General
State
CO
Basin
Gunnison
Water Division
4
Date
4/1/1997
Author
Mueller and Hiebert
Title
Assessment of Kokanee Salmon Transport through Blue Mesa Powerplant - Colorado - During the Spring and Summer of 1994-1996
Water Supply Pro - Doc Type
Report/Study
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<br />I <br /> <br />I <br /> <br />II <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />.' <br /> <br />. <br /> <br />I <br /> <br />. <br />I <br /> <br />II <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />n02~15 <br /> <br />early sieve netting when icing of the net might be minimal, could add <br />some valuable data to determine transport of overwintered kokanee. <br /> <br />Based on our preliminary findings and information from other sources, <br />fish losses appear to have less of an impact on the reservoir fishery <br />than possibly other factors such as actual harvest or predation. This <br />is not to say that significant losses couldn't occur in winter or <br />early spring, or under different operational and physical reservoir <br />conditions (i.e., surface spills or lower reservoir elevations). <br />Further monitoring and study are needed. <br /> <br />Fish Behavior and Facility Operational Considerations <br /> <br />Sieve netting below the powerplant indicated that the majority (96%) <br />of fish leaving the reservoir were small (30-120 mm) kokanee salmon. <br />This suggests that actual impacts to the creel may be delayed, <br />possibly as long as 2-3 years, the time necessary for these young fish <br />to reach harvestable size (CDOW reference). If the 1994 and 1995 <br />harvest declines did occur due to higher spring releases, young <br />kokanee would have had to have been transported in 1992 and 1993. <br /> <br />Hydroacoustic technology provides a valuable tool for measuring and <br />describing a pelagic fishery. Like all sampling techniques it <br />possesses specific strengths and weakness that need to be recognized <br />when reviewing the data. For instance, we 1I1ooked atll tens of <br />thousands of fish during the four field trips measuring actual fish <br />density (fish/mJ) and gathering information and relative fish size. <br />This simply would not be practical using conventional sampling <br />techniques. Also, fish found within the sound beam cannot evade <br />detection. Recent studies comparing acoustical and trawling <br />techniques showed that population estimates derived from acoustical <br />systems were typically 1.8 to 3.3 times greater than those calculated <br />from trawling data (Parkinson et al. 1994). Lower trawling estimates <br />were attributed to fish avoidance. <br /> <br />However, this technology does exhibit some "blind" spots. Fish found <br />within the littoral zone (<10 m), those found within 1.5 m of the <br />surface, 1 m of the bottom, or near submerged cover are not detected. <br />We are confident that adult kokanee population estimates accurately <br />describe those fish found in pelagic habitats at depths greater than <br />1.5 meters. <br /> <br />During August surveys, we observed large numbers of small kokanee <br />feeding near the surface where the zooplankton were swarming. Young <br />of the year kokanee can tolerate warmer temperatures than their adult <br />life stages. Fast growth during their first year must be attributed <br /> <br />31 <br />
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