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1 <br />3.5 Northern Pike Removal <br />3. S.1 Translocation of Northern Pike From Critical Habitat in the Yampa River (Project No. <br />98; CDOW, Larval Fish Laboratory/Colorado State University) <br />Northern pike were translocated from the Yampa River during 1999-2001. The purpose of the <br />translocation was to reduce risk of predation and competition of northern pike on endangered <br />Colorado pikeminnow. The objectives of the project were to (1) remove by translocation <br />northern pike from the Yampa River to Rio Blanco Reservoir (a small reservoir in the White <br />River drainage in northwestern Colorado), and (2) determine the effectiveness of removal <br />through length-frequency analysis and catch-per-unit-effort data. <br />Northern pike were first introduced into the Yampa River drainage in 1977 when 700 fish were <br />stocked by the Colorado Division of Wildlife into Elkhead Reservoir, an impoundment on <br />Elkhead Creek which is a tributary of the Yampa River just upstream of Craig, Colorado (Figure <br />10). The first northern pike were reported in the Yarnpa River in 1979, and guiding services for <br />anglers began in the 1980's (Figure 11). Elkhead Reservoir was drawn down in 1993 and again <br />in 1999, resulting in additional releases of fish into the Yampa River. Northern pike were <br />illegally released into Stagecoach Reservoir in about 1994, an impoundment on the Yampa River <br />upstream of Steamboat Springs, Colorado. <br />Northern pike were captured during four sampling occasions, each 11 days long. Sampling was <br />conducted during spring runoff when, adults were congregated to spawn in or near backwater <br />habitats. Shoreline electrofishing, block and shock, and fyke nets were used to capture fish <br />(Table 5). Shoreline electrofishing with one or two boats covered approximately 75 miles of <br />shoreline. A combination of electrofishing and trammel nets (i.e., block and shock) was used to <br />capture fish in backwaters, and fyke nets were set overnight in backwater habitats. <br />Although greater numbers of northern pike were captured in backwaters in the first three trips of <br />2000 (Figure 12), approximately half of all fish were captured in backwaters (52%) and about <br />half were captured in the main channel (48%). In 2001, 70% of the northern pike were captured <br />in the main channel and 30% were captured in backwaters: The majority of northern pike and <br />the majority of Colorado pikeminnow were captured with electrofishing (Figure 13). <br />A total of 784 northern pike were removed and translocated during 1999 2001, and 246 <br />Colorado pikeminnow were captured and released (Table 5). The ratio of northern pike to <br />Colorado pikeminnow ranged from 1.9:1.0 to 5.3:1.0, for an overall average of 3.2:1.0. A <br />notable change in the range of ratios occurred in the three sample sites between 1988-1991 <br />(1:1-4:1) and 1999-2000 (6:1-11:1). (Figure 14). Ratios for only two sites during 2001 were 2:1 <br />and 3:1, These data are inconclusive as to the trend of either species. <br />Length-frequency analysis of northern pike captured in 2000 and 2001 (Figure 15) showed a shift <br />to a higher mode in 2001; i.e., fish captured in 2001 were larger than those captured in 2000. <br />27 <br /> <br />~~ <br />1 <br /> <br />r- <br />J <br />1 <br /> <br /> <br /> <br />1 <br /> <br />1 <br /> <br />1 <br /> <br /> <br /> <br /> <br />