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~ may or may not be connected with the channel at low water, but which can be <br />connected at high water. These piscivorous fishes can displace native fishes and will <br />consume juveniles of the native fishes (Burdick 1996, Osmundson 1987). The third <br />group of nonnatives is a diverse collection of species (including channel catfish, black <br />bullheads, common carp, walleye, and northern pike) that are better adapted for <br />g riverine existence, and which may prey on native fishes in main channel habitat for part <br />or all of the year. Several of these nonnative species that pose problems in the UCRB <br />have been implicated in the demise of native fishes nationwide (ANSTF 1994). <br />The body of evidence documenting the deleterious effect of nonnatives on the native <br />~ fishes of the Colorado River system is sufficiently compelling to have convinced most <br />experts in the region. Hawkins and Nesler (1991) polled regional fisheries experts and <br />found that 81 % believed nonnative fishes were responsible for significant problems. <br />Maddux et al. (1993) reviewed issues related to the recovery of four endangered <br />Colorado fishes and reported that interactions with nonnatives were the primary factor <br />~ limiting recovery in some areas. Lentsch et al. (1996a) identified the nature of negative <br />interactions of many nonnatives with the endangered species. The nonnative fish issue <br />has been studied thoroughly (see review by Tyus and Saunders 1996a) and the <br />conclusions are clear that introduced species have played, and continue to play, a <br />significant role in the decline of the native big river fish community. <br />~ Species,specific Limiting Factors <br />Colorado pikeminnow <br />The specific factors regulating the growth and survival of adult Colorado pikeminnow <br />~ are not well known. Adults are probably not subject to predation because they are too <br />large for other piscivores to handle. Because the options for reducing adult mortality <br />are limited, the most feasible prospects for increasing the number of adults may lie in <br />improving or increasing their habitat, and this requires an understanding that habitat <br />has biological, as well as abiotic dimensions. <br />Adult nonspawning habitat. Studies in the UCR have shown that the best adult habitat <br />accessible to the extant population is in the reach from Westwater to Palisade (RM 125- <br />186). This conclusion was derived from data on fish abundance and condition from the <br />upper and lower portions of the Colorado River (Osmundson et al. 1997). Larger fish <br />~ move out of the lower UCR as they become subadults, and the few that remain tend to <br />be in poorer condition. In contrast, fish occupying the upper part of the UCR tend to <br />improve in condition as they grow larger. The logical inference is that the upper portion <br />(the 15-Mile Reach) offers better habitat conditions for the growth of adults than does <br />the remainder of the accessible portion of the UCR. That does not necessarily mean <br />~ that conditions in the 15-Mile Reach are optimal. <br />An examination of habitat use by adult Colorado pikeminnow shows that preferences <br />vary seasonally in the 15-Mile Reach (Osmundson et al. 1995). However, results of <br /> <br />28 <br /> <br />