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Final Programmatic Biological Opinion for Bureau of Reclamation's

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27During 1986-1988, 17 adult Colorado pikeminnow were captured in the 15-Mile Reach duringApril-June and radio-tagged. The fish exhibited a diversity <strong>of</strong> localized movements throughoutthe Grand Valley but spent a major part <strong>of</strong> their time in the 15-Mile Reach. Two remained in thereach throughout the estimated spawning period (Osmundson and Kaeding 1989).In a study by McAda and Kaeding (1991), a suspected prespawning aggregation <strong>of</strong> adultColorado pikeminnow was observed in mid-July <strong>of</strong> 1982 at river mile 178.3 in the 15-Mile Reach.In the first observation, three radio-tagged fish were tracked to one riverine pool area, and nineadults at or near spawning condition were then captured there after limited net sampling ef<strong>for</strong>ts.The aggregation occurred a few days after mean daily water temperature had reached 20 o C andduring a time when run<strong>of</strong>f flows were dropping <strong>of</strong>f sharply. A second aggregation was noted atriver mile 175.3, 12 days after the initial observation. Drifting trammel nets through an areaoccupied by two fish equipped with transmitters yielded an additional male Colorado pikeminnowin spawning condition. During this same time period, an adult female was captured near river mile175 that weighed nearly 1 pound more than when previously captured a month earlier, suggestingthe development <strong>of</strong> spawning (gravid) condition. Two Colorado pikeminnow larvae weresubsequently collected within the 15-Mile Reach.During 4 years (1982-1985) <strong>of</strong> larval sampling throughout the Grand Valley, 100 larvalpikeminnow were collected with fine-mesh hand nets from the two Colorado River reachesimmediately upstream and downstream <strong>of</strong> its confluence with the Gunnison River (McAda andKaeding 1991). Although the sampling ef<strong>for</strong>t was similar in the two river reaches, 98 percent <strong>of</strong>the larval captures occurred downstream <strong>of</strong> the Gunnison River confluence. Only two (2 percent)<strong>of</strong> the larvae were collected from the upstream reach. These observations may indicate that mostfish were spawned in the downstream reach or that the larvae were deposited in the upstreamreach and drifted downstream to the area where most <strong>of</strong> the captures were recorded. In 1995,drift nets set in the lower portion <strong>of</strong> the 15-Mile Reach captured 3 Colorado pikeminnow larvae(Anderson 1998).No postlarval young-<strong>of</strong>-year Colorado pikeminnow greater than 25 mm total length werecollected from above the Gunnison River confluence in fall collections from 1986-1994; however,one yearling-sized individual was captured there in 1986 (Osmundson and Burnham 1998). Atotal <strong>of</strong> 122 Colorado pikeminnow were collected in the 31-Mile Reach downstream <strong>of</strong> theconfluence <strong>of</strong> the Gunnison River during 1982-1996 (McAda and Ryel 1999). The 1982-1984catch rate <strong>of</strong> young-<strong>of</strong>-year Colorado pikeminnow in the 10-Mile Reach immediately downstream<strong>of</strong> the confluence <strong>of</strong> the Gunnison River (river miles 160-170) warranted classification <strong>of</strong> thisreach as a "Young-<strong>of</strong>-Year Nursery Area" by the Basin Biology Subcommittee (USFWS 1984).Catch rates <strong>of</strong> adult (> 500 mm long) Colorado pikeminnow in the 15- and 18-Mile Reaches <strong>of</strong>the Grand Valley are significantly higher than in any other portion <strong>of</strong> the Colorado River(Figure 1). In the 15-Mile Reach, adults are most abundant during spring in a 1.3-mile segmentbetween river miles 174.4 and 175.7, particularly in two gravel-pit ponds that were accessible

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