2001
DOI: 10.1002/etc.5620200604
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Effects of natural organic matter source on reducing metal toxicity to rainbow trout (Oncorhynchus mykiss) and on metal binding to their gills

Abstract: Juvenile rainbow trout (Oncorhynchus mykiss, 3 g) were exposed for 74 h in ion-poor (soft) water to a mixed-metal solution in the presence of 4, 6, and 10 mg C/L natural organic matter (NOM). The metals were 0.2 microM Pb, 0.1 microM Hg, 0.1 microM Cd, 1.3 microM Cu, 0.05 microM Ag, and 3.5 microM Co, and the natural organic matter was isolated by reverse osmosis from three sources in southern Ontario, Canada. The six-metal solution alone was extremely toxic to the fish. Increasing concentrations of each NOM i… Show more

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Cited by 93 publications
(67 citation statements)
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References 47 publications
(83 reference statements)
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“…elevation appears to have been negligible. Given the observed similarity in water chemistry of the exposure water in all other treatments, variability in Cu LC 50 to D. magna supports the source-dependent phenomenon reported earlier by Richards et al (2001), Ryan et al (2004), Schwartz et al (2004) andDe Schamphelaere et al (2004). In the following sections, the absorbance and fluorescence indices as quality predictors of DOMs are explored and discussed for their influence on the protective effect of DOMs against Cu toxicity (Cu LC 50 ) to D. magna.…”
Section: Resultssupporting
confidence: 66%
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“…elevation appears to have been negligible. Given the observed similarity in water chemistry of the exposure water in all other treatments, variability in Cu LC 50 to D. magna supports the source-dependent phenomenon reported earlier by Richards et al (2001), Ryan et al (2004), Schwartz et al (2004) andDe Schamphelaere et al (2004). In the following sections, the absorbance and fluorescence indices as quality predictors of DOMs are explored and discussed for their influence on the protective effect of DOMs against Cu toxicity (Cu LC 50 ) to D. magna.…”
Section: Resultssupporting
confidence: 66%
“…For multiple regression models, data for AHA were excluded from the analysis based on statistical criteria as outliers, especially for SAC 340 data, and the fact that AHA as a humic substance is not a real aquatic DOM (Malcolm and MacCarthy 1986). Since SAC 340 is supported by previous research for its strong influence on Cu toxicity (De Schamphelaere et al 2004;Richards et al 2001;Ryan et al 2004;Schwartz et al 2004), the method for placing SAC 340 in models was the forced entry, while backward stepwise entry was used for the other variables, according to the guidance of Field (2005). Although octanol solubility showed no correlation with LC 50 in the presence of 3 mg C l -1 , this quality parameter was also added to the aforementioned predictors based on its significant relationship with LC 50 at 6 mg C l -1 .…”
Section: Lc 50 Calculation and Statistical Analysesmentioning
confidence: 99%
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“…In fish, the embryonic and larval stages are usually the most sensitive to metals. The metal-gill interactions model takes into account metal speciation in water and the interactions between cations, anions, and organic ligands which can compete in solution for metals and decrease binding to the gill ligands (McGeer et al 2000;Richards et al 2001).…”
Section: Regardless Of Whether or Not The Observations Differmentioning
confidence: 99%