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Last modified
7/14/2009 5:02:36 PM
Creation date
5/20/2009 9:59:55 AM
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UCREFRP
UCREFRP Catalog Number
9591
Author
Nesler, T. P.
Title
Interactions Between Endangered Fishes and Introduced Gamefishs in the Colorado River, Colorado, 1986-1991.
USFW Year
2002.
USFW - Doc Type
91-29,
Copyright Material
NO
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<br />Black bullhead diet was similar to that of green sunfish, with aquatic insect larvae dominating <br />the non-fish prey items, which were found in 55% of all bullhead stomachs examined (Figure 15). <br />Unidentifiable fish and fish remains were the only type offish prey observed, occurring in 14.4% of <br />bullhead stomachs. Almost 31 % of black bullhead stomachs were empty. <br /> <br />The diet of channel catfish was also similar to the diets of black bullhead and green sunfish. <br />Non-fish prey items dominated stomach contents of catfish at 63% frequency of occurrence (Figure <br />15). Plant matter and aquatic insect nymphs and larvae were the most abundant non-fish food items <br />observed. Fish prey occurred in 11.3% of catfish examined and over half of these fish prey were <br />categorized as remains or unknown. Fathead minnow, red shiner and Gila sp. were the most <br />frequently occurring prey species in order of relative abundance. <br /> <br />DISCUSSION <br /> <br />Objective 1: to determine trends in abundance, distribution, reproductive success, and size <br />structure of non-native, non-saImonid gamef"lSh populations in the Colorado <br />River. <br /> <br />Results indicate that young-juvenile nonnative centrarchid gamefish were ubiquitous in <br />Colorado River backwaters, but represented a minor numerical component of the fish community, <br />During the study period, the relative abundance of all nonnative gamefish species actually <br />declined in backwaters, as did the relative abundance of native fish species. Results from ISMP <br />data subsequent to this study period (1993,1995, 1996, 1997) demonstrate nonnative gamefish <br />comprised only 0.6, 0.4, 2,0, and 11.3 percent of the samples for those four years, respectively <br />(McAda et al. 1994, 1996, 1997, 1998). The relative abundance of gamefish species overall and <br />for individual species in this investigation were similar to the ISMP results for these later years. <br />Green sunfish were most abundant for two out of the four years, and largemouth bass or black <br />bullhead were the most abundant in the other two years. <br /> <br />From a potential impact perspective, the relative abundance of fathead minnow, red shiner <br />and sand shiner suggests these species should be of much greater significance, both as competitors <br />and predators in comparison to nonnative gamefish species. ISMP results for years outside this <br />study period confrrm that the relative abundance of all species in this investigation is characteristic <br />of the fish composition in Colorado River backwaters. ISMP results from 1993 and 1995-1997 <br />demonstrate nonnative fish species comprised 87-96% of the fish sampled; and that red shiner, <br />fathead minnow and sand shiner made up 87-99 % of that nonnative fish population (McAda et al. <br />1994,1996, 1997, 1998). Bestgen et al. (1997) concluded "predation by red shiners may be a <br />major source of mortality for larval Colorado squawfish" based on model results. Conclusions from <br />Beyers et aI. (1994) for fathead minnow suggest competition between these species and Colorado <br />pikeminnow may be significant. McAda and Ryel (1999) showed catch rates of native fish species <br />were negatively correlated with the catch rates of red shiner, fathead minnow and sand shiner, and <br />positively correlated with Colorado pikeminnow. Catch rates among the three nonnative cyprinids <br />species were positively correlated. The authors attributed these results to the positive and negative <br /> <br />28 <br /> <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 />
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