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<br /> <br />B <br />-;z c;: <br /> <br />, \:, <br /> <br />,:.:~ <br /> <br />.; <br />.1~t <br /> <br />:J <br /> <br />/ /7<>ivf f fl:)I''''P/r-,(V ! <br /> <br />!:)'I~O _ <br /> <br />I <br />I <br />f <br />I <br />I <br />i <br />r <br />J <br /> <br />f :.' <br /> <br />" <br /> <br />r <br />r; <br />f <br />r <br />l <br /> <br />t ' <br /> <br />j' <br /> <br />JUNE 15, 1988 <br /> <br />EFFECTS OF COLD SHOCK ON COLORADO <br />SQUAWFISH LARVAE <br /> <br />CHARLES R. BERRY, JR. <br /> <br />ABSTRACT-Larvae oC Colorado squawCish (Ptychocheilus Lucius) acclimated to 220C were <br />subjected to water temperature decreases oC 5, 10, or 150C within 5 min or within 240 to 300 min. <br />Most mortality due 10 shock occurred in the Cirst 48 h. The 150C shock in 5 min caused <br />signiCicant mortality oC 14-day-old larvae but did not aHect 40-day-olds, In addition to causing <br />(his direct mortality, shocks oC 10 or 150C in 5 min caused behavioral changes in l4-day-olds that <br />could result in indirect mortality of wild Cish. <br /> <br />The Colorado squawfish (Ptychocheilus lucius) is endemic to the <br />Colorado River basin and historically was widely distributed in the <br />Colorado River and its major tributaries. After water developments on the <br />Colorado River system (Haynes et al., 1984), squawfish populations <br />declined; the species is now protected by the Endangered Species Act of <br />1973. One of several possible causes for this decline is lowered water <br />temperature below large dams (Miller, 1961; Marsh, 1985). <br />Water temperature from 20 to 260C is best for Colorado squawfish embryo <br />survival (Marsh, 1985), yearling growth (Black and Bulkley, 1985a) and <br />adult spawning (Haynes et aI., 1984). The final temperature preferendum of <br />yearlings is 250C, and larvae are usually collected where water temperatures <br />range from 19 to 260C (Haynes et al., 1984). Adult and yearling squawfish <br />can regulate somewhat the effect of water temperature change by avoiding \ <br />extremes, but passively drifting larval stages cannot. Therefore, larvae <br />drifting into any cold water plume could be adversely affected. Such a <br />situation could occur at the confluence of the Yampa and Green rivers. <br />Colorado squaw fish spawn in the lower Yampa River, and larvae drift into <br />the Green River, which is influenced by discharges from Flaming Gorge <br />Dam (Haynes et al., 1984; Tyus and McAda, 1984). No information on the <br />effects of rapidly decreasing water temperatures on Colorado squaw fish was <br />available, so I conducted a laboratory study to determine larval tolerance to <br />various cold shocks. <br /> <br />t, <br />~ . <br />'. <br /> <br />i <br />~ . <br />. ' <br />~ <br />r <br />I <br />I <br />i <br /> <br />, <br />I <br /> <br />I."" , <br />Li'. <br />~. ,.\ , ,", <br />j" ." ",. <br />, . <br /> <br />f " <br />I <br />I <br /> <br />MATERtALS AND METHODS-Cold shock experiments were conducted on 14-day-old (total length <br />9.0 :t 0.3 mm) squawCish larvae in 1984 and 1985 and on 40-day-old Cish (total length 24.4 :t 0.4 <br />mm) in 1984. Larvae Cound in the lower Yampa River in July 1981 by Haynes et al. (1984) ranged <br />in total length Crom 9 to 13 mm and in estimated age Crom 8 to 26 days old; hence, the 14-day- <br />old, 9-mm-long larvae used in this study Cairly represented wild Cish that might drift into the <br />Green River. Adults that produced larvae Cor my study were spawned, and eggs incubated, at the <br />Dexter (New Mexico) National Fish Hatchery. One-day-old sac Cry were air-shipped to Logan, <br />Utah, where they were held at the Utah Water Resources Research Laboratory at 220 in 74-1, f1ow- <br />through aquaria. Fish were Ced nauplii oC brine shrimp (Artemia). ad lib throughout the study. <br />Fish were counted and moved to bioassay aquaria by siphoning. <br />Bioassays were in 3.7-1 plastic aquaria receiving a continuous 0.25-l/min flow oC water <br />(hardness 174 mg/l; pH 7.1; dissolved oxygen 7.9 to 10.0 mg/l). Photoperiod was 14L:IOD. Two <br />aquaria with 100 larvae each were used Cor each treatment including controls in 1984, and three <br />aquaria with 50 larvae each in 1985. <br /> <br /> t. <br /> I. <br /> I <br />I I <br /> 0,' <br />I. . <br />I <br />, <br />i <br />! <br />