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<br />ri c\ I'Y\ llA C\.n <br />\q<b \ <br /> <br />()~7 ~~<6'~ <br /> <br />Hybridization of Three Species of Chub in a Hatchery <br /> <br />Three species of chub coexist in the Green and <br />Colorado rivers: bony tail chub (Gila elegans), hump- <br />back chub (G. cypha), and roundtail chub (G. <br />robusta). This Gila complex in the upper Colorado <br />River basin has often been troublesome to taxonomists. <br />Deacon et aI. (1979) listed the bony tail chub as an <br />endangered species in Arizona, California, Colorado, <br />Nevada, Utah, and Wyoming, and the humpback <br />chub in Arizona, Colorado, Utah, and Wyoming. <br />Both are listed as endangered species by the U.S. <br />Department of the Intcrior (1980). <br />Holden and Stalnaker (1970) found intergrades of <br />the round tail and bony tail chubs and of bony tail and <br />humpback chubs in the upper Colorado River basin; <br />intergrades of bony tail and humpback chubs were the <br />more numerous. Smith et al. (1979) suggested that <br />many specimens referred to by Holden and Stalnaker <br />as intergrades were, in fact, pure species. The purpose <br />of this study was to determine whether the bony tail <br />chub could hybridizc with the roundtail chub and <br />humpback chub. <br />Brood stock consistcd of five bony tail chub females, <br />eight round tail chub males, and five humpback chub <br />males. Bony tail chubs were collected from Lake <br />Mohave, near Cottonwood Cove, 30 April to I May <br />1979 and 29 April to 3 May 1980. The round tail and <br />humpback chubs werc collected from the Colorado <br />River, near Black Rocks, 5 November 1979. Total <br />lengths and weights of the collected specimens were <br />457 -559 mm and 850-1,300 g (bony tail), 298-352 mm <br />and 240-420 g (roundtail), and 304-330 mm and <br />275-385 g (humpback). <br />Because spawning temperatures range from 18 to <br />2loC (U.S. Fish and Wildlife Service 1979), incoming <br />hatchery water (12-130 C) was heated with a liquid <br />propane gas water heater (45,000 BTU/h), capable of <br />heating 23 L/min of incoming water to 20-2Ioe. The <br />heated water entered two ad jacen t concrete tanks (6 x <br />0.75 x 0.75 m) that scrved for recirculation, settling of <br />suspended matter, and aeration. Water was pumped at <br />132 L/ min from onc tank into the other by a 1/ 20-hp <br />fresh-f1o pump, and returned to the first tank by <br />gravity. Excess water escaped over a standpipe 70 cm <br />tall and 7.5 cm in diameter. Water was pumped from <br />these tanks with a I fJ-hp sump pump through 1.73-cm <br />polyvinyl chloride pipe with brass valves at a rate of <br />8 L/min to egg incubators and at 5 L/min to the two <br />broodstock tanks (6 x 0.75 x 0.75 m). Adult chubs <br />were held in the first tank, which contained (in the <br />upper half) cobblestones ranging in size from 50 to <br /> <br />140 <br /> <br />75 mm in diameter, through which water percolated to <br />create an artificial spawning environment. The cobble <br />was not used by the fish, however. <br />The egg incubators consisted of three alumlllum <br />troughs (3.5 x 0.55 x 0.30 m); two troughs received <br />heated water and the third received river water <br />(12-l30C). Hatching trays (53)( 53 cm) were covered <br />with lA-mm-mesh hardware cloth and slanted at a 300 <br />angle into the incoming water. <br />Ripening of sex products was induced by hormone <br />injection (Ihering 1937; Ball and Bacon 1954; Clemens <br />and Sneed 1962). Acetone-dried carp pituitary was <br />mixed with distilled water (40 mg/1O mL for the <br />bony tail x round tail cross) or with a solution of <br />oxytetracycline hydrochloride (40 mg(1O mL for the <br />bony tail x humpback cross). Before the intra- <br />peritoneal injections of 4 mg/ kg body weight, each <br />fish was anesthetized with tricaine methanesulfonate <br />at I :20,000 to I: 10,000 (Leitritz 1960). Injections were <br />repeated at 24-h intervals until the fish were ripe. <br />When eggs could be expelled with slight pressure, <br />the female was anesthetized and wiped dry and the <br />eggs were stripped into a plastic pa n. Milt from three <br />to four males was added to the eggs and water was then <br />added. When the eggs began to clump and adhere, they <br />were washed for 60 min, then separated. After samples <br />were taken to determine size, volume, and numbers, <br />the eggs were placed on screen trays for incubation and <br />hatching. <br />The day after swim up, fry were transferred to a cage <br />(I x I x I m, covered with 0.5-mm saran filter) in an <br />outside recirculating raceway. The fry were then fed a <br />starter trout diet and the natural zooplankton (pre- <br />dominately cIadocerans) that were present in the <br />raceway. <br /> <br />Bony tail chub x roundtail chub. All round tail males <br />produced milt of a low viscosity after two injections. <br />One bony tail female was ripe at the time of capture <br />and two became ripe 24 h after the first injection. Egg <br />diameters varied from 1.5 to 2.0 mm; the volume was <br />103 eggs/ mL. Fecundity was 15,862 and 20,806 in the <br />two injected females and 7,216 in the uninjected <br />female. Eggs from the uninjected female were infertile. <br />Eggs placed on slanted trays at 130 C developed very <br />slowly. Embryos formed by 96 h, but died after I 10 h. <br />The low water temperature is believed to have contribu- <br />ted to or caused the mortality. <br />Eggs placed on slanted trays at 200 C developed <br />more rapidly. The first cleavage was at 3.6 hand <br /> <br />Prog. Fish-Cult. 43(3), July 1981 <br />