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Last modified
7/14/2009 5:02:31 PM
Creation date
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UCREFRP
UCREFRP Catalog Number
7821
Author
Hamilton, S. J., et al.
Title
Evaluation Of Toxicity To Larval Razorback Sucker Of Selenium-Laden Food Organisms From Ouray NWR On The Green River, Utah.
USFW Year
1996.
USFW - Doc Type
\
Copyright Material
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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />1986, Besser et al. 1993, Saiki 1986, Sandholm et al. 1973) and its dietary toxicity at low <br />concentrations (Bennett et al. 1986, Hamilton et al. 1990, Hilton et al. 1980, Hodson and <br />Hilton 1983). Low waterborne selenium concentrations have been documented to adversely <br />affect reproduction in fish in experimental field studies (Hermanutz et al. 1992, Schultz and <br />Hermanutz 1990) and in environmental situations in Colorado (Barnhart 1957), North <br />Carolina (Cumbie and Van Horn 1978), and Texas (Garrett and Inman 1984, Sorensen <br />1988) . <br /> <br />The objective of the study was to evaluate the survival, growth, and whole-body <br />residues of selenium and other inorganics in larval razorback sucker exposed to reference <br />water and food organisms with naturally occurring selenium collected at Ouray NWR, Utah. <br />Wetlands in floodplains such as those found at Ouray are believed to be important nursery <br />habitats for larval razorback sucker (Modde et al. 1995, Tyus and Karp 1990) because of <br />their high invertebrate production (Mabey 1993). <br /> <br />:METHOD AND MATERIALS <br /> <br />The on-site toxicity investigation was conducted at the Ouray NWR, Utah, from May <br />21 to June 26, 1994, in a mobile laboratory transported from the Ecotoxicology Research <br />Station (ERS), Yankton, SD, and parked at the Ouray Native Fish Facility (Figure 2). Two <br />lots of larval razorback sucker were used in a total of four studies. One lot of larvae were <br />from adults spawned at Grand Junction, CO, from brood stock from Etter Pond near <br />DeBeque, CO. Fertilized eggs from this lot were transported to Ouray Native Fish Facility <br />where they were held before testing, and used in studies 1 and 2, which are described below. <br />Study 2 was initiated when unexpected mortality occurred in study 1 in larvae fed <br />zooplankton from the reference site. Following unexpected mortality in study 2 in larvae fed <br />zooplankton from the reference site, studies 3 and 4 were initiated and are described below. <br />There were insufficient larvae available from the first lot of larvae to conduct studies 3 or 4. <br />Consequently, a second lot of larvae from adults spawned at Ouray Native Fish Facility from <br />brood stock from the Colorado River arm of Lake Powell, was used in studies 3 and 4. <br /> <br />Larvae were cultured at Ouray Native Fish Facility in filtered river water (hardness <br />488 mg/L as CaC03, alkalinity 191 mg/L as CaC03, pH 8.0). Larvae from the first lot were <br />fed live nauplii of brine shrimp (Artemia sp.; Aquarium Products, Glen Bumie, MD) prior to <br />testing in studies 1 and 2. Larvae from the second lot were fed a commercial diet (Biokyowa <br />B-250 diet, Biodiet Products, Warrenton, OR) ad libitum prior to testing in studies 3 and 4. <br /> <br />Study 1 was initiated with 5-day-old larvae, study 2 with lO-day-old larvae, study 3 <br />with 24-day-old larvae, and study 4 with 28-day-old larvae. Ten fish were placed in each of <br />four replicate 2000-ml beakers containing 400 ml of filtered hatchery water and 400 ml of <br />Sheppard Bottom pond 1 (Sl) water to initiate acclimation. After 4 hours, an additional 800 <br />ml of S 1 water was added. Thereafter, fifty percent of the water was removed and replaced <br />daily with Sl water. All Sl water was filtered through a 153-Jlm mesh plankton net to <br />remove debris and plankton. Water in exposure beakers was aerated continuously with <br /> <br />4 <br />
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