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<br />Hypothesis of Historical Effects from Selenium <br /> <br />River Basin, con tracted in 1981 to have short-term tests conducted to deter- <br />mine the toxicity of selenium and several other inorganic and organic chemi- <br />cal constituents to sub-adult Colorado pikeminnow and humpback chub (Beleau <br />and Bartosz, 1982). Those tests seemed to indicate at the time that selenium <br />and other inorganic elements and organic chemicals were not contributing to <br />the decline of the species. However, the release of NIWQP reconnaissance <br />investigations of federal irrigation projects on the middle Green, upper Colo- <br />rado, Gunnison, Uncompahgre, and San Juan rivers reported elevated sele- <br />nium concentrations in water and biota. Consequently, additional toxicity tests <br />were conducted with several early life stages of Colorado pike minnow, razor- <br />back sucker, bonytail, and tlannelmouth sucker in water qualities simulating <br />environmental conditions (Hamilton, 1995; Buhl and Hamilton, 1996; Buhl, <br />1997; Hamilton and Buhl, 1997a, 1997b). In these short-term tests, the endan- <br />gered fish had similar sensitivity to selenate, selenite, and other elements as <br />other fish species. However, tests with environmentally relevant mixtures of <br />inorganic elements showed a high hazard was present in some areas of the <br />Green River and San Juan River basins. <br />Long-term tests with larval razorback sucker and bonytail exposed to an <br />environmental mixture of inorganic elements including selenium and tested <br />in a reconstituted Green River water showed adverse effects at concentrations <br />less than 10-fold of the environmental concentrations, which suggested a high <br />hazard (Hamilton et al., 2000). In another long-term study, larval razorback <br />sucker were fed live zooplankton collected from six sites at Ouray National <br />Wildlife Refuge (NWR), Ouray, UT, adjacent to the Green River, that con- <br />tained different amounts of selenium. Survival was 0 to 20% in four studies <br />initiated with larvae aged 5, 10, 24, and 28 days old (Hamilton et al., 1996). <br />Both of the Ashley Creek and Ouray NWR studies showed adverse effects on <br />larval razorback sucker at selenium concentrations presently in the upper <br />Colorado River basin. <br />Elevated selenium concentrations in muscle plugs, eggs, and lcuvae from <br />wild razorback sucker have been documented in adults inhabiting areas known <br />to have elevated selenium concentrations in water and biota such as Ashley <br />Creek and Stewart Lake outlet on the Green River (Waddell and May, 1995; <br />Hamilton and Waddell, 1994; Stephens and Waddell, 1998; Hamilton et al., <br />1998). A similar pattern of elevated selenium residues in muscle plugs of <br />Colorado pikeminnow collected from areas with elevated selenium in water <br />and food organisms was found in the upper Colorado River (Osmundson, <br />May, and Osmundson, 1999). These selenium residues in razorback sucker <br />and Colorado pikeminnow show that endangered fish in high selenium areas <br />were accumulating selenium to concentrations that could harm their repro- <br />ductive success. <br /> <br />mSTORICAL OCCURRENCE OF ENDANGERED FISH <br /> <br />Colorado pikeminnow and razorback sucker were abundant in the upper <br />Colorado River basin according to Jordan (1891) during a survey of streams <br /> <br />, <br />Hum. Ecol. Risk Assess. Vol. 5, No.6, 1999 <br /> <br />1165 <br />