Serveur d'exploration sur l'esturgeon

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Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures.

Identifieur interne : 000212 ( PubMed/Checkpoint ); précédent : 000211; suivant : 000213

Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures.

Auteurs : Robin D. Calfee [États-Unis] ; Edward E. Little ; Holly J. Puglis ; Erinn Scott ; William G. Brumbaugh ; Christopher A. Mebane

Source :

RBID : pubmed:25043712

English descriptors

Abstract

The acute toxicity of cadmium, copper, and zinc to white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) were determined for 7 developmental life stages in flow-through water-only exposures. Metal toxicity varied by species and by life stage. Rainbow trout were more sensitive to cadmium than white sturgeon across all life stages, with median effect concentrations (hardness-normalized EC50s) ranging from 1.47 µg Cd/L to 2.62 µg Cd/L with sensitivity remaining consistent during later stages of development. Rainbow trout at 46 d posthatch (dph) ranked at the 2nd percentile of a compiled database for Cd species sensitivity distribution with an EC50 of 1.46 µg Cd/L and 72 dph sturgeon ranked at the 19th percentile (EC50 of 3.02 µg Cd/L). White sturgeon were more sensitive to copper than rainbow trout in 5 of the 7 life stages tested with biotic ligand model (BLM)-normalized EC50s ranging from 1.51 µg Cu/L to 21.9 µg Cu/L. In turn, rainbow trout at 74 dph and 95 dph were more sensitive to copper than white sturgeon at 72 dph and 89 dph, indicating sturgeon become more tolerant in older life stages, whereas older trout become more sensitive to copper exposure. White sturgeon at 2 dph, 16 dph, and 30 dph ranked in the lower percentiles of a compiled database for copper species sensitivity distribution, ranking at the 3rd (2 dph), 5th (16 dph), and 10th (30 dph) percentiles. White sturgeon were more sensitive to zinc than rainbow trout for 1 out of 7 life stages tested (2 dph with an biotic ligand model-normalized EC50 of 209 µg Zn/L) and ranked in the 1st percentile of a compiled database for zinc species sensitivity distribution.

DOI: 10.1002/etc.2684
PubMed: 25043712


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pubmed:25043712

Le document en format XML

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<div type="abstract" xml:lang="en">The acute toxicity of cadmium, copper, and zinc to white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) were determined for 7 developmental life stages in flow-through water-only exposures. Metal toxicity varied by species and by life stage. Rainbow trout were more sensitive to cadmium than white sturgeon across all life stages, with median effect concentrations (hardness-normalized EC50s) ranging from 1.47 µg Cd/L to 2.62 µg Cd/L with sensitivity remaining consistent during later stages of development. Rainbow trout at 46 d posthatch (dph) ranked at the 2nd percentile of a compiled database for Cd species sensitivity distribution with an EC50 of 1.46 µg Cd/L and 72 dph sturgeon ranked at the 19th percentile (EC50 of 3.02 µg Cd/L). White sturgeon were more sensitive to copper than rainbow trout in 5 of the 7 life stages tested with biotic ligand model (BLM)-normalized EC50s ranging from 1.51 µg Cu/L to 21.9 µg Cu/L. In turn, rainbow trout at 74 dph and 95 dph were more sensitive to copper than white sturgeon at 72 dph and 89 dph, indicating sturgeon become more tolerant in older life stages, whereas older trout become more sensitive to copper exposure. White sturgeon at 2 dph, 16 dph, and 30 dph ranked in the lower percentiles of a compiled database for copper species sensitivity distribution, ranking at the 3rd (2 dph), 5th (16 dph), and 10th (30 dph) percentiles. White sturgeon were more sensitive to zinc than rainbow trout for 1 out of 7 life stages tested (2 dph with an biotic ligand model-normalized EC50 of 209 µg Zn/L) and ranked in the 1st percentile of a compiled database for zinc species sensitivity distribution.</div>
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<AbstractText>The acute toxicity of cadmium, copper, and zinc to white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) were determined for 7 developmental life stages in flow-through water-only exposures. Metal toxicity varied by species and by life stage. Rainbow trout were more sensitive to cadmium than white sturgeon across all life stages, with median effect concentrations (hardness-normalized EC50s) ranging from 1.47 µg Cd/L to 2.62 µg Cd/L with sensitivity remaining consistent during later stages of development. Rainbow trout at 46 d posthatch (dph) ranked at the 2nd percentile of a compiled database for Cd species sensitivity distribution with an EC50 of 1.46 µg Cd/L and 72 dph sturgeon ranked at the 19th percentile (EC50 of 3.02 µg Cd/L). White sturgeon were more sensitive to copper than rainbow trout in 5 of the 7 life stages tested with biotic ligand model (BLM)-normalized EC50s ranging from 1.51 µg Cu/L to 21.9 µg Cu/L. In turn, rainbow trout at 74 dph and 95 dph were more sensitive to copper than white sturgeon at 72 dph and 89 dph, indicating sturgeon become more tolerant in older life stages, whereas older trout become more sensitive to copper exposure. White sturgeon at 2 dph, 16 dph, and 30 dph ranked in the lower percentiles of a compiled database for copper species sensitivity distribution, ranking at the 3rd (2 dph), 5th (16 dph), and 10th (30 dph) percentiles. White sturgeon were more sensitive to zinc than rainbow trout for 1 out of 7 life stages tested (2 dph with an biotic ligand model-normalized EC50 of 209 µg Zn/L) and ranked in the 1st percentile of a compiled database for zinc species sensitivity distribution.</AbstractText>
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<RefSource>Environ Toxicol Chem. 2001 Jul;20(7):1421-37</RefSource>
<PMID Version="1">11434282</PMID>
</CommentsCorrections>
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<RefSource>Environ Toxicol Chem. 2001 Oct;20(10):2397-402</RefSource>
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<CommentsCorrections RefType="Cites">
<RefSource>Environ Sci Pollut Res Int. 2014;21(13):8176-87</RefSource>
<PMID Version="1">24920427</PMID>
</CommentsCorrections>
<CommentsCorrections RefType="Cites">
<RefSource>Ecotoxicology. 2013 Jan;22(1):139-47</RefSource>
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<CommentsCorrections RefType="Cites">
<RefSource>Arch Environ Contam Toxicol. 2012 Oct;63(3):400-8</RefSource>
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<CommentsCorrections RefType="Cites">
<RefSource>Environ Toxicol Chem. 2012 Apr;31(4):689-90; author reply 690-2</RefSource>
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<RefSource>Arch Environ Contam Toxicol. 2005 Feb;48(2):143-54</RefSource>
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<CommentsCorrections RefType="Cites">
<RefSource>Fundam Appl Toxicol. 1982 Mar-Apr;2(2):67-72</RefSource>
<PMID Version="1">7185603</PMID>
</CommentsCorrections>
<CommentsCorrections RefType="Cites">
<RefSource>Toxicol Appl Pharmacol. 1975 Sep;33(3):471-83</RefSource>
<PMID Version="1">1188945</PMID>
</CommentsCorrections>
<CommentsCorrections RefType="Cites">
<RefSource>Aquat Toxicol. 2004 Jul 14;68(4):369-92</RefSource>
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</CommentsCorrections>
<CommentsCorrections RefType="Cites">
<RefSource>Comp Biochem Physiol C Toxicol Pharmacol. 2002 Sep;133(1-2):287-303</RefSource>
<PMID Version="1">12356534</PMID>
</CommentsCorrections>
<CommentsCorrections RefType="Cites">
<RefSource>Environ Toxicol Chem. 2014 Oct;33(10):2246-58</RefSource>
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