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<br />\ <br /> <br />'c <br /> <br />I. ABSTRACT <br /> <br />The declining numbers of some endemic Colorado River fishes is attributed to low <br />or the complete lack of recruitment. Although the long-lived endangered fishes <br />spawn successfully and produce 1 arvae, high mortal ity during the early 1 ife <br />stages limits recruitment with the result that some native fish stocks are no <br />longer self-sustaining. Four native fishes (razorback sucker, bony tail , humpback <br />chub, and Colorado squawfi sh) are 1 i sted as endangered under the Endangered <br />Speci es Act. <br /> <br />The Biology Committee members have agreed that Colorado squawfish and humpback <br />chub stocks below impassable barriers appear to be stable and recruitment has <br />been documented (Wydoski 1994). However, it is not known with certainty whether <br />present recruitment is adequate to maintain self-sustaining populations. The <br />bony tail has declined to the point where only occasional specimens are captured <br />in the upper basin with long periods of time and long distances between captures. <br />Potential hybridization of bony tail with other Gila in the upper basin poses <br />genetic risks that may limit reintroduction efforts of the bony tail into its <br />historic range. <br /> <br />The razorback sucker is considered the primary species where recovery efforts may <br />re-establish the species in the Upper Colorado River and restore the remaining <br />middle Green River stock (Wydoski 1994). Enhancement or restoration of <br />fl oodp 1 a in habitats through reconnect i on wi th upper bas i n ri vers wi 11 improve the <br />productivity of the ecosystem for zooplankton and benthic invertebrates required <br />by the early life stages of the razorback sucker. Any enhancement or restoration <br />endeavors must be made through experiments that are thoroughly evaluated using <br />the adaptive management approach. Attempts to restore large areas of floodplain <br />habitats would preclude adequate evaluations and refinements using the adaptive <br />management approach. Limited areas that are enhanced or restored shoul d be <br />thoroughly evaluated and refinements made as necessary to determine the responses <br />of the endangered and nonnative fishes to such efforts. <br /> <br />The removal of levees that are on the lowest floodplain terraces, coupled with <br />higher spring streamflow releases that mimic the historic hydrographs from <br />upstream dams, provide the best way to reconnect mainstem and tributary rivers <br />with product i ve fl oodp la ins. Such removal should be done on low fl oodp 1 a in <br />terraces on pub 1 i c propert i es that can be eas il y reconnected wi th the ma in <br />channel and where thorough evaluations can be made. Experiments on publ ic <br />property would preclude extremely high releases that would cause sociological <br />problems associating with the flooding of private agricultural lands and the <br />production of mosquitoes that could pose human health problems. If the <br />experiments performed on public property are successful and it is determined that <br />more floodplain habitat is needed for restoration, then leasing of private lands <br />can be explored and implemented. <br /> <br />However, some nonnative fi shes that are estab 1 i shed in the upper bas in will <br />flourish in productive off-channel habitats. If the duration of inundation of <br />off-channel habitats is short, razorback suckers will not grow to a size where <br />predation and competition by nonnative fishes is no longer a principal factor in <br />their survival. If the duration of flooding these habitats is longer, nonnative <br />fishes will flourish and continue to adversely affect larval and juvenile <br />razorback suckers. These nonnative fish interactions may limit the recovery of <br />the razorback sucker unless adequate control measures can be implemented in <br />