1992
DOI: 10.1007/bf00212269
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Estimation of waterborne selenium concentrations that are toxicity thresholds for wildlife

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Cited by 58 publications
(32 citation statements)
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“…In addition to the work of Lemly, TETs have been reported by others (Table 1), and these include TETs for water (Peterson and Nebeker 1992; U.S. Environmental Protection Agency 2005), sediment , and fish diet, wholebody fish, and fish ovaries (DeForest et al 1999;Skorupa et al 1996). Whereas the TET for water has been determined at 2 μg/L by Lemly (2002) and Peterson and Nebeker (1992), the U.S. Environmental Protection Agency (2005) has established a criteria continuous concentration (CCC) of 5 μg/L for total recoverable selenium in water.…”
Section: Assessment Of Data With Other Toxic Effect Thresholdsmentioning
confidence: 98%
See 2 more Smart Citations
“…In addition to the work of Lemly, TETs have been reported by others (Table 1), and these include TETs for water (Peterson and Nebeker 1992; U.S. Environmental Protection Agency 2005), sediment , and fish diet, wholebody fish, and fish ovaries (DeForest et al 1999;Skorupa et al 1996). Whereas the TET for water has been determined at 2 μg/L by Lemly (2002) and Peterson and Nebeker (1992), the U.S. Environmental Protection Agency (2005) has established a criteria continuous concentration (CCC) of 5 μg/L for total recoverable selenium in water.…”
Section: Assessment Of Data With Other Toxic Effect Thresholdsmentioning
confidence: 98%
“…Whereas the TET for water has been determined at 2 μg/L by Lemly (2002) and Peterson and Nebeker (1992), the U.S. Environmental Protection Agency (2005) has established a criteria continuous concentration (CCC) of 5 μg/L for total recoverable selenium in water. For the North Fork, 31 out of 45 collected water samples (69%) exhibited selenium concentrations exceeding 5 μg/L.…”
Section: Assessment Of Data With Other Toxic Effect Thresholdsmentioning
confidence: 99%
See 1 more Smart Citation
“…Subsequent research on selenium indicated that food-chain bioaccumulation, dietary intake, and reproductive effects should be given high priority in hazard assessment (Woock and Summers, 1984;Garrett and Inman, 1984;Sorensen et al, 1984;Lemly, 1985aLemly, , 1985bBaumann and Gillespie, 1986;Gillespie and Baumann, 1986;Heinz et al, 1987). Utilizing this and other information, some investigators have developed mathematical models to describe and predict selenium cycling and toxicity (e.g., Porcella et al, 1991;Peterson and Nebeker, 1992;Bowie and Grieb, 199 1;Bowie, 1995). Models can be a useful tool for predicting toxicological risk.…”
Section: Introductionmentioning
confidence: 99%
“…Despite the large amount of new toxicity information generated during the past decade (e.g., USFWS, 1990aUSFWS, , 1990bFigure l), and the need to evaluate selenium hazards at many locations across the U.S. (Peterson and Nebeker, 1992;Presser et al, 1994;Seiler and Skorupa, 1995), there is no common assessment method in use. This has resulted in confusion and frustration for those involved in hazard assessment of both site-specific and regional selenium contamination problems (Sylvester et al, 1991;Presser et al, 1994).…”
Section: Introductionmentioning
confidence: 99%