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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />4.3.4.2 Foraee. Competition. and Predation. Colorado squawfish can become piscivorous in their <br />first year of life, and retain a nearly exclusive fISh diet throughout life (Valdez 1990). Non-native <br />cyprinids (i.e. red shiner, sand shiner, and fathead minnow) can probably provide an ample forage <br />base for juvenile squawfish. An. ample forage base of both native and non-native fish is available for <br />adult squawflSh in the system. <br /> <br />Non-native cyprinids in the Dolores River appear to be no greater a potential threat to Colorado <br />squawfish than in other rivers in the Upper Colorado River Basin. These non-natives may be a <br />source of competition to larval squawfish, but their abundance in nursery habitat (backwaters) is no <br />higher than other areas on the Colorado and Green rivers which consistently harbor young squawfish. <br />The diet of these non-natives is probably adult and immature insects, small crustaceans, and plant <br />material (Pflieger 1975), although recent data from the Yampa River suggest that red shiners may <br />be piscivorous on larval native species (J. Ruppert, CSU, Pers. Comm. Feb. 1992). Effects of <br />predation by these species on Colorado squawfish are not known (Valdez 1990). Green sunfish are <br />highly piscivorous and represent a potential threat, but these fish are found in small numbers in the <br />Dolores River, mostly near the Colorado River confluence. Other centrarchids (e.g., bluegill, <br />largemouth bass) were rare in the Dolores River. Ictalurids probably represent the most significant <br />potential threat to squawfish in the Dolores River. Black bullheads are probably indiscriminate <br />feeders, and even small numbers may constitute a threat to small fish. Only 48 bullheads were <br />captured in 1990-1991. These were found mostly along shorelines, rather than in backwaters, perhaps <br />tempering their threat to young squawfish. Channel catfish are also piscivorous, and juvenile and <br />adults have been found in sympatry with chubs in Cataract Canyon (Valdez 1990). Channel catfish <br />in the Dolores River were collected in greater numbers from eddies and shorelines than from <br />backwaters, possibly reducing the potential for larval squawflSh predation. Predation by large adult <br />catfish on juvenile and small adult squawfish is a potential problem, although relatively few large adult <br />catfish were captured in 1990-1991. Trout are rare in the Dolores River below Disappointment <br />Creek and probably have little effect on squawfish. <br /> <br />4.4 Feasibility of Reintroducing Colorado SquawOsh <br /> <br />Data collected on physical, chemical and biological attributes of the Dolores River during this <br />study suggest that reintroduction of Colorado squawfish into the Dolores River system is possible. <br />However, since the status of the species in the Upper Colorado River is not fully understood and <br />further study is required to determine the extent that Colorado squawfish use the Dolores River, <br />reintroduction of squawfish for purposes of augmenting populations is not recommended. Based on <br />results of this study, it is recommended that the Dolores River drainage be considered as a site for <br />experimental stocking of Colorado squawfish and possibly razorback sucker associated with future <br />research. With low numbers of squawfish currently in the drainage and few predators relative to <br />other upper basin drainages, the Dolores would be suitable for experimental stocking. Potential <br />research includes studies on survival, dispersal and homing of various life stages of the species. <br />BIO/WEST recognizes three potential experimental scenarios that would be feasible in the Dolores <br />River drainage. These include: 1) incubation of eggs in situ; 2) release of PIT-tagged juveniles, and; <br />3) chemoreception studies with adults. <br /> <br />4.4.1 Incubation of Eggs in Situ <br /> <br />Reintroduction via incubation of eggs in situ has not been attempted for endangered species in <br />the upper basin of the Colorado River. The possibility of strong homing tendencies by these species, <br />especially Colorado squawfish, suggests that this type of reintroduction may be suitable for re- <br />establishing drainage-specific stocks. A well conceived study that would allow the incubation and <br /> <br />23 <br />