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<br />I <br /> <br /> <br />.r-....., <br />'. <br /> <br /> <br /> <br /> <br />Jel <br />I <br />1.-1 <br /> <br />'. <br /> <br /> <br /> <br />'I <br />fI <br /> <br />5. The Role of Stocking in Management and Recovery <br /> <br />fI <br /> <br />The primary purpose of stocking endangered fish is to reestablish populations. Whether stocking simply <br />maintains a presence for the species or establishes self sustaining communities is dependent on the species' <br />ability to adapt and reproduce under existing environmental conditions. The reintroduction of native fishes <br />back into their historical ranges seems fairly straight forward, however, we seldom recognize all the factors that <br />caused their original demise. 'Three decades of stocking endangered fishes has shown that unless these <br />bottlenecks are identified and adequately addressed, recruitment failure will continue to occur. <br />Millions of small razorbacks have been stocked in the mainstream and larger tributaries with little or no <br />success. Predation is undoubtedly a major factor attributing to loses. Studies conducted in the upper basin <br />have found a similar correlation of size with survival (Burdick 2003). Burdick recommended that only suckers <br />>20 cm be stocked and that the role of site acclimation and survival be further investigated. Marsh and Brooks <br />(1989) recommended similar actions in the lower basin nearly 15 years earlier. <br />During the past decade, more than 85,000 larger (>25 cm) suckers have been stocked in an attempt to <br />counter predation losses, but unfortunately, survival rates continue to remain low and may be less than 10%. <br />Survivors have either joined or created new spawning communities. These fish are starting to spawn and while <br />larvae have been detected, natural recruitment has not. Young natives continue to fall victim to predators. <br />One of the primary challenges in measuring stocking survival is to recapture adequate numbers of fish. <br />Unfortunately, this has been difficult due primarily to poor survival. Initial information suggests current <br />augmentation efforts for the razorback sucker are falling substantially short (> 15%) of expected survival and <br />repopulation goals. Even less information is available for the bonytail. We simply are unsure whether our <br />sampling programs are ineffective or the fish simply have not survived. <br />Poor survival combined by the outcome of the telemetry experiments raises doubt regarding the <br />performance of hatchery-reared fish and our percei ved notion these communities can co-exist with sport fishes. <br />After nearly two decades, it appears a reassessment of goals and objectives, as well as the stocking location <br />and methods being used to rear and reintroduce fish are warranted. This chapter provides some alternative <br />methods that may increase the likelihood of recruitment and discusses other associated issues. <br /> <br />II <br />~I <br /> <br />'...'.1.'. <br />\ <br />I <br />t <br /> <br />[I <br />,I <br />~I <br />,I <br />I <br />'I <br />I <br />I <br /> <br />Bony tail, Flannelmouth, and Razorback Suckers: Contrasting Survival Stories <br /> <br />The tlannelmouth sucker represents the first successful reintroduction of a native fish in the main stem <br />Colorado River. Historically they were rare in the mainstem with only five collections documented prior to <br />1975 (Minckley, 1973). A single stocking of611 tlannelmouths and the thousands of razorback suckers that <br />were stocked presents an interesting and revealing paradox. <br />The rapid success of the flannel mouth in view of the stocking failure of razorbacks has prompted biologists <br />to ask why flannelmouths could survive and produce young when razorback ,suckers have not. Both the <br />tlannelmouth and razorback are similar in size, color, and shape and evolved in the Colorado River. So why <br />has the flannelmouth, which was historically rare, out performed the razorback which was once abundant in the <br />main stem? <br />The answer may lay in the dramatic physical and biological changes that have taken place in the main stem <br />river. It also raises some impelling questions regarding stocking philosophies, targeted species, predator/prey <br />relationships, and the role of physical habitat. <br /> <br />Stocking Comparisons <br /> <br />The first obvious difference in the stocking approaches is the source of the fish. Wild fish taken from the <br />Paria River were used to stock flannelmouth while bonytail and razorback suckers that were stocked were <br />produced in hatcheries. The wild suckers undoubtedly possessed survival skills that the hatchery-reared fish <br />did not. They were accustomed to flow, finding natural foods, and recognizing and avoiding predators. Their <br /> <br />25 <br />