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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 />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 />cohorts into a notable adult population in the river or in backwaters. <br /> <br />Meals and Miranda (1991) observed that age-O bluegill and crappie migrate from littoral <br />habitats to limnetic zones a few days after hatching, while largemouth bass stay in the littoral <br />zone. These traits may help explain the presence of largemouth bass and the comparative scarcity <br />of bluegill and black crappie in the "littoral habitat" present in Colorado River backwaters. <br />According to Meals and Miranda (1991), bluegill leave the shallows at < 11 mm and return at <br />sizes between 11-25 mm. Bluegill progeny deposited or spawned in Colorado River backwaters <br />would be unlikely to survive and return to a backwater habitat after leaving. Black crappie at 45- <br />60 mm leave littoral habitats for deep water. There is no surrogate for deepwater lentic habitat <br />in the Colorado River. The lotic habitat and fluctuating backwater habitat of the Colorado River <br />likely promote high mortality for bluegill, black crappie and their progeny. Largemouth bass <br />young would tend to stay put in backwater habitats and persist as long as favorable conditions <br />existed. <br /> <br />Sample results targeting larger-bodied fish indicate that channel catfish and common cazp <br />were the most abundant adult fish in Colorado River backwaters, at least during April and July. <br />Native adult fish appear to use the backwaters in the spring only. Mainchannel fish sampling <br />data, however, demonstrates a different picture of relative abundance from backwater sampling. <br />Using dipnet, seine and electrofishing in the Colorado River from RMI 149-170 in 1983, Wick <br />et al. (1985) captured roundtail chub, speckled dace, flannelmouth sucker, bluehead sucker <br />comprising 74% of the total sample, whereas common carp and channel catfish were much less <br />common at 5 and 0.4% of the catch. Anderson and Stewart (2000, 2001) estimated channel <br />catfish at 195-660 fishlkm and common carp at 300-590 ftsh/km in the 15Mi1e-Reach of the <br />Colorado River in 1999-2000. The relative abundance of select fish species in the Anderson and <br />Stewart samples were channel catfish (4-14%), common catp (11-16%), flannelmouth sucker (31- <br />38 %), bluehead sucker (23-40 %) and roundtail chub at 3-7 %. Relative abundance of backwater <br />species indicate nearly complete dominance by nonnative cyprinids and channel catfish, whereas <br />relative abundance of mainchannel adult fish populations suggests native species are more <br />abundant. Similar contrasts between backwater and mainchannel fish communities were found <br />by Anderson (1997) in the Colorado River above the study site and by Burdick (1995) in the <br />Gunnison River above Red1ands diversion dam near the Colorado River confluence. Osmundson <br />(1999) reported bluehead and flannelmouth sucker as the most abundant fish species collected in <br />the Colorado River from Palisade, Colorado to the confluence with the Green River in Utah. <br />Anderson and Stewart (2002, in draft) report flannelmouth and bluehead sucker > 150 nun long <br />as the most abundant in the Colorado River in the 15-mile reach. <br /> <br />Despite the apparent concentration of adult channel catfish in the Colorado River <br />backwaters based on blocknet sampling, and the densities of adult channel catfish reported by <br />Anderson and Stewart (2000, 2001), young-of-year (YOY) of this species were relatively scarce <br />in fall backwater seine samples. It is possible that this life stage of catfish may be using riffle-run <br />habitat during daylight hours, and/or may become more active in backwater habitats during <br />crepuscular periods. This diel behavior would account for their relative scarcity in daytime seine <br /> <br />33 <br />
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