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1.1 Background <br />This project was justified based on a belief that entrenched, existing programs are causing <br />institutional resistance to consolidating and integrating historical and new research into a <br />comprehensive description of the linkages among selenium, water development, and wildlife. <br />Selenium toxicity is presumed to be the primary cause of avian teratogenesis at the Kesterson <br />National Wildlife Refuge and some other locations in the western United States. Selenium <br />toxicity also has been implicated in the collapse of several populations of endangered fish <br />(Bureau of Reclamation 1998). The premise for ascribing the poisoning to selenium has its <br />origin, in part, on the belief that a livestock disease called blind staggers was caused by selenium <br />(Beath et al. 1953). High concentrations of selenium in animal tissue and the abundance of <br />seleniferous plants were related to blind staggers. Consequently, selenium tissue concentrations <br />have been used to guide recent investigations and programs related to the recovery of endangered <br />fish such as the Colorado River squawfish (now pikeminnow) and. the razorback sucker. The role <br />of selenium, however, is disputed as shown by recent publications advocating a much higher <br />standard for protection of aquatic life in western streams (Canton 1999). <br />Research published in the veterinary literature suggests that blind staggers in cattle is not caused <br />by selenium but by sulfate and other factors associated with high salt/alkaline soils (O'Toole and <br />Raisbeck 1995). This research also shows that selenium causes sterility but is not teratogenic to <br />livestock. Other work shows that pronghorn, indigenous to high selenium locales, tolerate <br />relatively high levels of selenium in their blood, and that mallards confined to a high selenium <br />diet would starve rather than eat the food (Raisbeck et al. 1996). Taken together, these data <br />suggest that the original premise implicating selenium could be overemphasized. Moreover, the <br />data suggest that indigenous, endangered fish in the intermountain West also could be relatively <br />tolerant of selenium. Indeed, the fish recovery programs are guided to some extent by selenium <br />analyses of tissue plugs, a practice that the veterinary research refutes in mammals (O'Toole and <br />Raisbeck 1995). <br />Researchers have also been monitoring and reporting changes within the Colorado River system <br />(Van Steeter and Pitlick 1998). Recent published reports show that the Colorado River, in the <br />Grand Valley, has lost approximately 30% of its average flow in the past 40 years. The average <br />width of the river has decreased by approximately 60 ft in the same time period. Aerial photos <br />show that the complexity of the habitat associated with the river also has declined at a significant <br />rate. Furthermore, the preceding documented changes do not address the considerable alterations <br />to the flow regime (suppressing spring runoff, prolonging summer/fall runoff, decreasing <br />sediment load, decreasing summer temperature, increasing winter temperature) caused by water <br />diversions and. dams. <br />1.2 Project Scope <br />This project was supported from the Seed Money Fund of the Laboratory Directed Research and <br />Development Program at Oak Ridge National Laboratory. The project funding of approximately <br />$14,000 resulted in a limited scope that included a comprehensive literature search, in-depth <br />interviews with researchers in the field (Table 1), and a field survey of habitat in the Grand <br />Valley. Those contacted are listed in Table 1.