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<br />the Yampa River in April and May. All fish were implanted with coded wire tags prior to <br />stocking. No fish were implanted with radio tags. <br /> <br />Obiective 2: Determine the appropriate number and size of bony tail to stock to maximize <br />survival. <br /> <br />Recaptures <br /> <br />Recapture effort summaries <br /> <br />The total effort expended on the Colorado River was as follows: electrofishing (EL) 99.45 hrs, <br />seining (SN) 69 habitats, fyke/hoop nets (FN/HN) 131 net nights, and 66 trammel sets (Table 2). <br />Monitoring on the Colorado River began the fall of 1996 and concluded in the fall of 200 1. The <br />methods applied and the river miles covered varied widely from year to year, depending on <br />additional work loads and available personnel. <br /> <br />The total effort expended in the lower Green River was: EL 359.95 hrs, SN 42 habitats, FN/HN 9 <br />net nights, and 9 trammel sets (Table 2). Monitoring in the Green River began in the spring of <br />1999 and concluded in the summer of 2002. As was the case in the Colorado River, sampling <br />methods and the area covered varied year to year. Also of note, in 2000, 2001, and 2002 a <br />portion of the sampling occurred prior to the spring stocking events. This early sampling allowed <br />for some assessment of bonytail overwintering success. Bonytail collected during pre-stocking <br />sampling had persisted through at least one winter and potentially more. <br /> <br />Total recaptures <br /> <br />Over the course of all sampling in the Colorado River, 1996-2001, a total of 663 hatchery-reared <br />bonytail were recaptured, representing 0.8% of all fish released (Table 3). Seventeen (0.02%) of <br />the fish recaptured in the Colorado River had overwintered and persisted in the system for more <br />than six months. Most of the long-term recaptures in the Colorado occurred in 2001 (Table 4). <br />In the Green River, a total of 523 or 0.4% of the stocked bonytail were recaptured between 1999 <br />and 2002. Of the Green River recaptures, 59 fish (0.05%) had overwintered and persisted in the <br />system for more than 6 months. As in the Colorado River, the majority (31) of the long-term <br />recaptures in the Green River occurred in 2001 (Table 4). <br /> <br />Other native fish stocking efforts have experienced similar overall recapture rates when stocking <br />juvenile fish. Age-O Colorado pikeminnow (mean TL 24-55mm) stocked in the San Juan River <br />showed an overall return rate of 0.3-0.5% and approximately 0.096.10 for fish at large for 6 months <br />or more (Archer et al. 2000). Overall 0.4-0.8% of juvenile (mean TL < 300 mm) razorback <br />sucker (Xyrauchen texanus) cohorts stocked in the upper Colorado, Gunnison, and San Juan <br />rivers were recaptured (Burdick 2002; Ryden 2000). For juvenile razorbacks at large more than 6 <br />months 0.1 % were recaptured in the upper Colorado and Gunnison rivers, and 0.3% were <br />recaptured in the San Juan River. In contrast, for adult sized razorbacks (mean TL > 300 mm) in <br /> <br />9 <br />