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Last modified
7/14/2009 5:01:43 PM
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5/20/2009 5:15:00 PM
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UCREFRP
UCREFRP Catalog Number
3022
Author
Berry, C. R. and R. Pimentel
Title
Swimming Performances of Three Rare Colorado River Fishes
USFW Year
1985
USFW - Doc Type
Transactions of the American Fisheries Society
Copyright Material
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<br />400 <br /> <br />BERRY AND PIMENTEL <br /> <br />TABLE 2.-Prolonged swimming performance of several freshwater fishes, expressed as body lengths (BL) per <br />second and its equivalent absolute swimming speed. <br /> Temper- Prolonged speed <br /> T otallength ature <br />Species (cm) ("C) BUs cm/s Source <br />Atlantic salmon \~ <br />Salmo salar 23 15 2.1-3.2 50-76 Kutty and Saunders (1973) <br />Largemouth bass <br />Micropterus salmoides 14-27 20 2.3-3.0 45-63 Beamish (1970) <br />Smallmouth bass <br />Micropterus dolomeiu 5-6 20 3.3-5.4 19-31 Larimore and Duever (1968) <br />Coho salmon <br />Oncorhynchus kisutch 6-9 20 4.6-5.4 31-41 Brett et al. (1958) <br />Rainbow trout <br />Salmo gairdneri 6 20 4.1-7.1 25-43 Butler and Milleman (1971) <br /> <br />al. 1958). Our data for the humpback and bony- <br />tail chubs are consistent with this generalization <br />(Fig. 1). The small Colorado squawfish per- <br />formed better at 260C than at 20oC, but their <br />intermediate performance at 140C confounded <br />the trend. Large Colorado squawfish did not im- <br />prove performance with increase in tempera- <br />ture-an unexpected result that may have been <br />related to the small sample size or to the possible <br />inaccuracy of estimates made without fatigue data <br />between 0 and 100% (Stephan 1977). <br />We noticed great variation among individuals <br />in swimming ability, especially at intermediate <br />velocities. Such variability has been noted by <br />others (McNeish and Hatch 1978; Kovacs and <br />Leduc 1982) and probably represents different <br />levels of motivation, stress, and ability within <br />each species. <br /> <br />Discussion <br />These rare Colorado River fishes have biolog- <br />ical traits that may confer survival advantages <br />in swift, sometimes turbulent waters (Minckley <br />1973). The narrow caudal peduncle and high as- <br />pect ratio (square of the maximum fin height <br />divided by the fin area) of the caudal fin of the <br />humpback and bonytai1 chubs suggest superior <br />swimming ability compared with that of other <br />species (Lighthill 1969). Although the ability of <br />these two species was greater than that of the <br />Colorado squawflsh of similar size, their pro- <br />longed swimming performance at 200C was sim- <br />ilar to that of some other fishes (Table 2). A <br />downward bias to our data may have resulted <br />from the use of unexercised fish (Webb 1975) <br /> <br />and from our use of a sudden velocity increase, <br />instead ofthe gradually increasing velocities used <br />in other tests. <br />The final temperature preferendum for these <br />species is 24-250C (Bulkley et al. 1981). It is <br />generally assumed that the final preferendum is <br />the optimum temperature for most physiological <br />functions of fish. Hence, the swimming perfor- <br />mance of these species at 260C was probably near <br />maximum, although this conclusion is specula- <br />tive because stamina was not evaluated at higher <br />temperatures. Maximum prolonged swimming <br />of other eurytherma1 species usually occurs at <br />temperatures between 25 and 300C (Beamish <br />1978). <br />Hydroelectric plants and other industrial com- <br />plexes remove water at structures that are po- <br />tential sites for entrainment and impingement of <br />young fish. Recommended approach and screen- <br />face velocities at intakes are about 15 cm/s <br />(Barnes 1976). The 120-min FV50 for small fish <br />exceeded 35 cm/s at all temperatures; conse- <br />quently the fish tested in our study should be <br />able to avoid entrainment. However, larvae may <br />be the most vulnerable life stage, and there is no <br />published information on their swimming abil- <br />ity. <br />Fish passage must be provided to preserve mi- <br />grating species such as the potamodromous Col- <br />orado squawfish, which undertakes spawning <br />migrations of several hundred kilometres (Tyus <br />1983). Fish ladders have been suggested as a pos- <br />sible conservation measure because the northern <br />squawfish Ptychocheilus oregonensis readily uses <br />fish ladders on the Columbia River (Clay 1961; <br /> <br />{ <br />
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