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<br />\l q S <,lit1fYl i I J1J 11 jStt>>G <br /> <br />ECOTOXICOLOGY AND ENVIRONMENTAL SAFETY 30, 134-142 (1995) <br /> <br />q'lf1 <br /> <br />Hazard Assessment of Inorganics to Three Endangered Fish in the <br />Green River, Utah <br /> <br />STEVEN J . HAMILTON <br /> <br />National Biological Survey, National Fisheries Contaminant Research Center, Field Research Station, RR 1, Box 295, Yankton, <br />South Dakota 57078-9214 <br /> <br />Received January 24, 1994 <br /> <br />Acute toxicity tests were conducted with three life stages of <br />Colorado squawfish (Ptychocheilus Lucius), razorback sucker <br />(Xyrauchen texanus), and bonytail (Gila elegans) in a reconsti- <br />tuted water quality simulating the middle part of the Green River <br />of Utah. Tests were conducted with boron; lithium, selenate, sel- <br />enite, uranium, vanadium, and zinc. The overaU rank order of <br />toxicity to all species and life stages combined from most to least <br />toxic was vanadium = zinc > selenite > lithium = uranium > <br />selenate> boron. There was no difference between the three spe- <br />cies in their sensitivity to the seven inorganics based on a rank- <br />order evaluation at the species level. Colorado squawfish were 2-5 <br />times more sensitive to selenate and selenite at the swimup life <br />stage than older stages, whereas razorback suckers displayed <br />equal sensitivity among life stages. Bonytail exhibited equal sen- <br />sitivity to selenite, but were five times more sensitive to selenate at <br />the swimup life stage than the older stages. Comparison of 96-hr <br />LCso values with a limited number of environmental water con- <br />centrations in Ashley Creek, Utah, which receives irrigation <br />drainwater, revealed moderate hazard ratios for boron, selenate, <br />selenite, and zinc, low hazard ratios for uranium and vanadium, <br />but unknown ratios for lithium. These inorganic contaminants in <br />drainwaters may adversely affect endangered fish in the Green <br />River. 0 1995 Academic Press, Inc. v <br /> <br />INTRODUCTION <br /> <br />After the discovery of contaminated irrigation return <br />waters in the San Joaquin Valley of central California in <br />1982 (Ohlendorf et aL., 1986; Saiki, 1986), the Department <br />of the Interior (DOl) initiated a program to.identify other <br />irrigation drainages in the western United States with <br />similar water quality problems. These investigations fo- <br />cused on DOl irrigation projects, where the receiving <br />water was a national wildlife refuge or had the potential <br />to impact migratory birds or endangered species. The <br />Green River, located in northeastern Utah, was identified <br />as one area needing further study. <br />The Green River provides sensitive habitats for the <br />Colorado squawfish (Ptychocheilus Lucius), razorback <br />sucker (Xyrauchen texanus), and bony tail (Gila elegans). <br />These species are listed as endangered under the provi- <br />sions of the Endangered Species Act of 1973 (USFWS, <br /> <br />0147-6513/95 $6.00 <br />Copyright'" 1995 by Academic Press. Inc. <br />All rights of reproduction in any fonn reserved. <br /> <br />1974, 1980, 1991). For Colorado squawfish and razorback <br />suckers, spawning areas are limited (Tyus, 1990; Tyus <br />and Karp, 1990), and the critical life stages are those from <br />fertilized eggs through the first year (Miller et al., 1982). <br />The Green River near Jensen, Utah, is a known spawning <br />location for razorback suckers with staging occurring in <br />Ashley Creek and Stewart Lake outlet (Tyus and Karp, <br />1990). Young-of-year Colorado squawftsh~~:razorback <br />suckers use shallow alongshore embaY!ne.n~Qutsery <br />habitats (Tyus, 1987; Tyus and Haines, 1991l};and these <br />habitats occur at and below the mouth of Ashley Creek <br />and the Stewart Lake outlet where irrigation return flows <br />are concentrated. Little information is available about the <br />distribution, abundance, or habitat use by bony tail (Tyus <br />and Karp, 1989). <br />The DOl irrigation drainwater investigation of the mid- <br />dle Green River basin (Stephens et al., 1988; Peltz and <br />Waddell, 1991) reported that selenium concentrations in <br />waters supplying Stewart Lake, the mouth of Ashley <br />Creek, and one pond at Ouray National Wildlife Refuge <br />were four to six times greater than the 20,..J.I.~{ef"acute <br />limit (l-hr average not to be exceeded once every 3 years) <br />established for the protection of aquatic organisms; the <br />chronic limit (4-day average not to be exceeded every 3 <br />years) is 5 ~g/liter (USEPA, 1987). They also reported <br />that boron, selenium, and zinc concentrations in water, <br />bottom sediment, and biological tissues were sufficiently <br />large to be harmful to fish and wildlife. <br />The purpose of this study was to determine the acute <br />toxicity of boron, lithium, selenate, selenite, uranium, <br />vanadium, and zinc to early life stages of Colorado <br />squawfish, razorback sucker, and bony tail in a water <br />quality simulating the middle Green River. The acute tox- <br />icity values were then compared with environmental con- <br />centrations of these inorganics found in various waters in <br />the middle Green River to assess their potential hazard to <br />endangered fish. <br /> <br />MATERIALS AND METHODS <br /> <br />Eyed-eggs of Colorado squawflsh, razorback sucker, <br />and bony tail were obtained from Dexter National Fish <br /> <br />134 <br />