Speciation, behavior, and bioavailability of copper downstream of a mine-impacted lake
A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine‐impacted lake (East Lake, ON, Canada). Elevated levels (∼50 μg/L) of Cu exist in th...
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Published in: | Environmental toxicology and chemistry Vol. 26; no. 12; pp. 2594 - 2603 |
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Wiley Periodicals, Inc
01-12-2007
Blackwell Publishing Ltd |
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Abstract | A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine‐impacted lake (East Lake, ON, Canada). Elevated levels (∼50 μg/L) of Cu exist in the lake due to the release of dissolved Cu to the water column from underlying sediments. Most of the Cu present in East Lake and downstream is present as filterable species that represent 74 to 100% of the total. Measurements of labile Cu as measured by diffusive gradients in thin films (DGT) suggest that most of the Cu is unavailable to aquatic biota. The DGT results indicate that 9 to 24% of Cu within the receiving environment is biologically available. Decreases in the labile Cu fraction with distance downstream of East Lake correlate well with increases in the concentration of DOC (r2 = 0.79–0.95), presumably due to the progressive importance of Cu‐organic complexes. The relationship between filterable Cu and SO2−4 downstream of East Lake was linear (r2 = 0.99) for all sampling periods, suggesting that decreases in filterable Cu concentration downstream of East Lake could be attributed solely to dilution (i.e., conservative behavior). Variations in the filterable Cu concentration resulting in 50% mortality (LC50 = 96–203 μg/L) and the concentration resulting in an inhibition of reproduction by 25% (IC25 = 75–156 μg/L) with respect to Ceriodaphnia dubia (7‐d incubation) in Cu‐spiked solutions could be explained by differences in labile‐Cu concentrations as determined by DGT. The considerable complexation capacity afforded by lake and stream waters can be attributed to complexation of Cu with abundant DOC (7–17 mg/L). The relevance of the toxicity data to water‐effect ratio testwork, and the associated development of site‐specific water quality objectives, are discussed. |
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AbstractList | A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine-impacted lake (East Lake, ON, Canada). Elevated levels (approximately 50 microg/L) of Cu exist in the lake due to the release of dissolved Cu to the water column from underlying sediments. Most of the Cu present in East Lake and downstream is present as filterable species that represent 74 to 100% of the total. Measurements of labile Cu as measured by diffusive gradients in thin films (DGT) suggest that most of the Cu is unavailable to aquatic biota. The DGT results indicate that 9 to 24% of Cu within the receiving environment is biologically available. Decreases in the labile Cu fraction with distance downstream of East Lake correlate well with increases in the concentration of DOC (r(2) = 0.79-0.95), presumably due to the progressive importance of Cu-organic complexes. The relationship between filterable Cu and SO(4)(2-) downstream of East Lake was linear (r(2) = 0.99) for all sampling periods, suggesting that decreases in filterable Cu concentration downstream of East Lake could be attributed solely to dilution (i.e., conservative behavior). Variations in the filterable Cu concentration resulting in 50% mortality (LC50 = 96-203 microg/L) and the concentration resulting in an inhibition of reproduction by 25% (IC25 = 75-156 microg/L) with respect to Ceriodaphnia dubia (7-d incubation) in Cu-spiked solutions could be explained by differences in labile-Cu concentrations as determined by DGT. The considerable complexation capacity afforded by lake and stream waters can be attributed to complexation of Cu with abundant DOC (7-17 mg/L). The relevance of the toxicity data to water-effect ratio testwork, and the associated development of site-specific water quality objectives, are discussed. A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine-impacted lake (East Lake, ON, Canada). Elevated levels (~50 µg/L) of Cu exist in the lake due to the release of dissolved Cu to the water column from underlying sediments. Most of the Cu present in East Lake and downstream is present as filterable species that represent 74 to 100% of the total. Measurements of labile Cu as measured by diffusive gradients in thin films (DGT) suggest that most of the Cu is unavailable to aquatic biota. The DGT results indicate that 9 to 24% of Cu within the receiving environment is biologically available. Decreases in the labile Cu fraction with distance downstream of East Lake correlate well with increases in the concentration of DOC (r^sup 2^ = 0.79-0.95), presumably due to the progressive importance of Cu-organic complexes. The relationship between filterable Cu and SO^sup 2-^^sub 4^ downstream of East Lake was linear (r^sup 2^ = 0.99) for all sampling periods, suggesting that decreases in filterable Cu concentration downstream of East Lake could be attributed solely to dilution (i.e., conservative behavior). Variations in the filterable Cu concentration resulting in 50% mortality (LC50 = 96-203 µg/L) and the concentration resulting in an inhibition of reproduction by 25% (IC25 = 75-156 µg/L) with respect to Ceriodaphnia dubia (7-d incubation) in Cu-spiked solutions could be explained by differences in labile-Cu concentrations as determined by DGT. The considerable complexation capacity afforded by lake and stream waters can be attributed to complexation of Cu with abundant DOC (7-17 mg/L). The relevance of the toxicity data to water-effect ratio testwork, and the associated development of site-specific water quality objectives, are discussed. [PUBLICATION ABSTRACT] A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine- impacted lake (East Lake, ON, Canada). Elevated levels (sim50 mu g/L) of Cu exist in the lake due to the release of dissolved Cu to the water column from underlying sediments. Most of the Cu present in East Lake and downstream is present as filterable species that represent 74 to 100% of the total. Measurements of labile Cu as measured by diffusive gradients in thin films (DGT) suggest that most of the Cu is unavailable to aquatic biota. The DGT results indicate that 9 to 24% of Cu within the receiving environment is biologically available. Decreases in the labile Cu fraction with distance downstream of East Lake correlate well with increases in the concentration of DOC (r super(2) = 0.79-0.95), presumably due to the progressive importance of Cu-organic complexes. The relationship between filterable Cu and SO sub(4) super(2- ) downstream of East Lake was linear (r super(2) = 0.99) for all sampling periods, suggesting that decreases in filterable Cu concentration downstream of East Lake could be attributed solely to dilution (i.e., conservative behavior). Variations in the filterable Cu concentration resulting in 50% mortality (LC50 = 96-203 mu g/L) and the concentration resulting in an inhibition of reproduction by 25% (IC25 = 75-156 mu g/L) with respect to Ceriodaphnia dubia (7-d incubation) in Cu-spiked solutions could be explained by differences in labile-Cu concentrations as determined by DGT. The considerable complexation capacity afforded by lake and stream waters can be attributed to complexation of Cu with abundant DOC (7-17 mg/L). The relevance of the toxicity data to water-effect ratio testwork, and the associated development of site-specific water quality objectives, are discussed. A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine‐impacted lake (East Lake, ON, Canada). Elevated levels (∼50 μg/L) of Cu exist in the lake due to the release of dissolved Cu to the water column from underlying sediments. Most of the Cu present in East Lake and downstream is present as filterable species that represent 74 to 100% of the total. Measurements of labile Cu as measured by diffusive gradients in thin films (DGT) suggest that most of the Cu is unavailable to aquatic biota. The DGT results indicate that 9 to 24% of Cu within the receiving environment is biologically available. Decreases in the labile Cu fraction with distance downstream of East Lake correlate well with increases in the concentration of DOC ( r 2 = 0.79–0.95), presumably due to the progressive importance of Cu‐organic complexes. The relationship between filterable Cu and SO 2− 4 downstream of East Lake was linear ( r 2 = 0.99) for all sampling periods, suggesting that decreases in filterable Cu concentration downstream of East Lake could be attributed solely to dilution (i.e., conservative behavior). Variations in the filterable Cu concentration resulting in 50% mortality (LC50 = 96–203 μg/L) and the concentration resulting in an inhibition of reproduction by 25% (IC25 = 75–156 μg/L) with respect to Ceriodaphnia dubia (7‐d incubation) in Cu‐spiked solutions could be explained by differences in labile‐Cu concentrations as determined by DGT. The considerable complexation capacity afforded by lake and stream waters can be attributed to complexation of Cu with abundant DOC (7–17 mg/L). The relevance of the toxicity data to water‐effect ratio testwork, and the associated development of site‐specific water quality objectives, are discussed. A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine-impacted lake (East Lake, ON, Canada). Elevated levels (~50 mug/L) of Cu exist in the lake due to the release of dissolved Cu to the water column from underlying sediments. Most of the Cu present in East Lake and downstream is present as filterable species that represent 74 to 100% of the total. Measurements of labile Cu as measured by diffusive gradients in thin films (DGT) suggest that most of the Cu is unavailable to aquatic biota. The DGT results indicate that 9 to 24% of Cu within the receiving environment is biologically available. Decreases in the labile Cu fraction with distance downstream of East Lake correlate well with increases in the concentration of DOC (r2 = 0.79-0.95), presumably due to the progressive importance of Cu-organic complexes. The relationship between filterable Cu and SO42- downstream of East Lake was linear (r2 0.99) for all sampling periods, suggesting that decreases in filterable Cu concentration downstream of East Lake could be attributed solely to dilution (i.e., conservative behavior). Variations in the filterable Cu concentration resulting in 50% mortality (LC50 = 96-203 mug/L) and the concentration resulting in an inhibition of reproduction by 25% (IC25 = 75-156 mug/L) with respect to Ceriodaphnia dubia (7-d incubation) in Cu-spiked solutions could be explained by differences in labile-Cu concentrations as determined by DGT. The considerable complexation capacity afforded by lake and stream waters can be attributed to complexation of Cu with abundant DOC (7-17 mg/L). The relevance of the toxicity data to water-effect ratio testwork, and the associated development of site-specific water quality objectives, are discussed. A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system rich in dissolved organic carbon (DOC) downstream of a mine‐impacted lake (East Lake, ON, Canada). Elevated levels (∼50 μg/L) of Cu exist in the lake due to the release of dissolved Cu to the water column from underlying sediments. Most of the Cu present in East Lake and downstream is present as filterable species that represent 74 to 100% of the total. Measurements of labile Cu as measured by diffusive gradients in thin films (DGT) suggest that most of the Cu is unavailable to aquatic biota. The DGT results indicate that 9 to 24% of Cu within the receiving environment is biologically available. Decreases in the labile Cu fraction with distance downstream of East Lake correlate well with increases in the concentration of DOC (r2 = 0.79–0.95), presumably due to the progressive importance of Cu‐organic complexes. The relationship between filterable Cu and SO2−4 downstream of East Lake was linear (r2 = 0.99) for all sampling periods, suggesting that decreases in filterable Cu concentration downstream of East Lake could be attributed solely to dilution (i.e., conservative behavior). Variations in the filterable Cu concentration resulting in 50% mortality (LC50 = 96–203 μg/L) and the concentration resulting in an inhibition of reproduction by 25% (IC25 = 75–156 μg/L) with respect to Ceriodaphnia dubia (7‐d incubation) in Cu‐spiked solutions could be explained by differences in labile‐Cu concentrations as determined by DGT. The considerable complexation capacity afforded by lake and stream waters can be attributed to complexation of Cu with abundant DOC (7–17 mg/L). The relevance of the toxicity data to water‐effect ratio testwork, and the associated development of site‐specific water quality objectives, are discussed. Speciation, behavior, and bioavailability of copper (Cu) downstream of a mine-impacted lake were investigated. Sulfate concentrations were measured using a Dionex ion chromatograph with a chemically suppressed conductivity detector. The toxicity data for C. dubia in Cu-spiked solutions showed that chronic and acute toxicity varied by at least a factor of two on a seasonal basis. The temporal and spatial variability in Cu bioavailability emphasized the importance of site-specific variables that contributed to assimilative capacity. It was concluded as the part of management measures designed to ensure the protection of aquatic resources that diffusive gradients in thin films (DGT) showed to be a useful tool for the development of site-specific water quality objectives. |
Author | Goldblatt, Robert Martin, Alan J. |
Author_xml | – sequence: 1 fullname: Martin, A.J – sequence: 2 fullname: Goldblatt, R |
BackLink | https://www.ncbi.nlm.nih.gov/pubmed/18020684$$D View this record in MEDLINE/PubMed |
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Copyright | Copyright © 2007 SETAC Copyright Alliance Communications Group, A Division of Allen Press, Inc. Dec 2007 |
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Snippet | A combination of Cu speciation analysis and toxicity testwork was conducted to assess the behavior, speciation, and bioavailability of Cu in a stream system... Speciation, behavior, and bioavailability of copper (Cu) downstream of a mine-impacted lake were investigated. Sulfate concentrations were measured using a... |
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SubjectTerms | animal reproduction Animals Aquaculture Aquatic animals aquatic arthropods Bioavailability Biological Assay Biological Availability Biota Canada Ceriodaphnia dubia chemical speciation Cladocera - drug effects Copper Copper - analysis Copper - toxicity Daphnia - drug effects Diffusive gradients diffusivity Discharge Dissolved organic carbon Drainage ecotoxicology Environmental Monitoring filtration Lakes Lethal Dose 50 Membranes, Artificial Minerals Mining Reproducibility of Results sediment contamination sediments Soils solutions Speciation Specimen Handling streams sulfates Surface Properties Thin films toxicity testing Toxicity Tests, Acute Water column Water effect ratio Water Pollutants, Chemical - analysis Water Pollutants, Chemical - toxicity Water pollution Water quality |
Title | Speciation, behavior, and bioavailability of copper downstream of a mine-impacted lake |
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