TY - JOUR
T1 - Trophic transfer of Cd from larval chironomids (Chironomus riparius) exposed via sediment or waterborne routes, to zebrafish (Danio rerio)
T2 - Tissue-specific and subcellular comparisons
AU - Béchard, K. M.
AU - Gillis, P. L.
AU - Wood, C. M.
N1 - Funding Information:
USEPA, 2000. Update of Ambient Water Quality Criteria for Cadmium. U.S. Environmental Protection Agency Office of Water Office of Science and Technology, Washington, DC (EPA Contract No. 68-C-98-134).
Funding Information:
We thank Jennifer Webber of Environment Canada for supplying us with C. riparius egg masses to start our culture, Dr. K. Liber for advice on pore water sampling, and Dr. T. Ng, P. Craig and E. Leonard for assistance in the lab. We would also like to thank Dr. Peter Chapman of Golder Associates, for providing comments on the manuscript. This work was supported by the NSERC CRD Program, the International Lead Zinc Research Organization, the International Zinc Association, the Nickel Producers Environmental Research Association, the International Copper Association, the Copper Development Association, Teck-Cominco, Xstrata (Noranda-Falconbridge), and Inco. CMW is supported by the Canada Research Chair Program.
PY - 2008/12/11
Y1 - 2008/12/11
N2 - Zebrafish were fed chironomid larvae (8% wet weight daily ration) for 7 days, followed by 3 days of gut clearance in a static-renewal system. Regardless of whether the chironomids had been loaded with Cd via a waterborne exposure or sediment exposure, they had similar subcellular distributions of Cd, with the largest areas of storage being metal rich granules (MRG) > organelles (ORG) > enzymes (ENZ) except that sediment-exposed chironomids had significantly more Cd in the metallothionein-like protein (MTLP) fraction, and significantly less Cd in the cellular debris (CD) fraction. When zebrafish fed sediment-exposed chironomids (153 ± 11 μg Cd/g dry weight) were compared directly to zebrafish fed waterborne exposed chironomids (288 ± 12 μg Cd/g dry weight), identical whole-body Cd levels were observed, despite the difference in the concentration in the food source. Thus trophic transfer efficiency (TTE) of Cd was significantly greater from sediment-exposed chironomids (2.0 ± 0.5%) than from waterborne-exposed chironomids (0.7 ± 0.2%). Subsequent tests with waterborne exposed chironomids loaded to comparable Cd concentrations, as well as with Cd-spiked manufactured pellets, demonstrated that TTEs were concentration-independent. In all treatments, zebrafish exhibited similar subcellular storage of Cd, with the greatest uptake occurring in the ORG fraction followed by the ENZ fraction. However, neither trophically available metal (TAM) nor metabolically available fractions (MAF) were good predictors for the TTEs found in this study. Tissue Cd concentrations were highest in the kidney and gut tissue, then liver, but lower in the gill, and carcass. Overall, the gut and carcass contributed ≥71% to total body burdens on a mass-weighted basis. This study presents evidence that Cd may be acquired by fish from natural diets at levels of environmental relevance for contaminated sites, and that the exposure route of the prey influences the TTE.
AB - Zebrafish were fed chironomid larvae (8% wet weight daily ration) for 7 days, followed by 3 days of gut clearance in a static-renewal system. Regardless of whether the chironomids had been loaded with Cd via a waterborne exposure or sediment exposure, they had similar subcellular distributions of Cd, with the largest areas of storage being metal rich granules (MRG) > organelles (ORG) > enzymes (ENZ) except that sediment-exposed chironomids had significantly more Cd in the metallothionein-like protein (MTLP) fraction, and significantly less Cd in the cellular debris (CD) fraction. When zebrafish fed sediment-exposed chironomids (153 ± 11 μg Cd/g dry weight) were compared directly to zebrafish fed waterborne exposed chironomids (288 ± 12 μg Cd/g dry weight), identical whole-body Cd levels were observed, despite the difference in the concentration in the food source. Thus trophic transfer efficiency (TTE) of Cd was significantly greater from sediment-exposed chironomids (2.0 ± 0.5%) than from waterborne-exposed chironomids (0.7 ± 0.2%). Subsequent tests with waterborne exposed chironomids loaded to comparable Cd concentrations, as well as with Cd-spiked manufactured pellets, demonstrated that TTEs were concentration-independent. In all treatments, zebrafish exhibited similar subcellular storage of Cd, with the greatest uptake occurring in the ORG fraction followed by the ENZ fraction. However, neither trophically available metal (TAM) nor metabolically available fractions (MAF) were good predictors for the TTEs found in this study. Tissue Cd concentrations were highest in the kidney and gut tissue, then liver, but lower in the gill, and carcass. Overall, the gut and carcass contributed ≥71% to total body burdens on a mass-weighted basis. This study presents evidence that Cd may be acquired by fish from natural diets at levels of environmental relevance for contaminated sites, and that the exposure route of the prey influences the TTE.
KW - Cadmium
KW - Chironomus riparius
KW - Danio rerio
KW - Metal accumulation
KW - Subcellular distribution
KW - Tissue-specific distribution
KW - Trophic transfer
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UR - http://www.scopus.com/inward/citedby.url?scp=56349141076&partnerID=8YFLogxK
U2 - 10.1016/j.aquatox.2008.07.014
DO - 10.1016/j.aquatox.2008.07.014
M3 - Article
C2 - 18950874
AN - SCOPUS:56349141076
VL - 90
SP - 310
EP - 321
JO - Aquatic Toxicology
JF - Aquatic Toxicology
SN - 0166-445X
IS - 4
ER -