Annual Review
Physiological changes and tissue metal accumulation in rainbow trout exposed to foodborne and waterborne metals
Article first published online: 21 OCT 2009
DOI: 10.1002/etc.5620131215
Copyright © 1994 SETAC
Additional Information
How to Cite
Farag, A. M., Boese, C. J., Bergman, H. L. and Woodward, D.F. (1994), Physiological changes and tissue metal accumulation in rainbow trout exposed to foodborne and waterborne metals. Environmental Toxicology and Chemistry, 13: 2021–2029. doi: 10.1002/etc.5620131215
Publication History
- Issue published online: 21 OCT 2009
- Article first published online: 21 OCT 2009
- Manuscript Accepted: 17 JUN 1994
- Manuscript Received: 30 MAR 1994
- Abstract
- References
- Cited By
Keywords:
- Rainbow trout;
- Ionoregulation;
- Scale loss;
- Lipid peroxidation;
- Tissue metals
Abstract
Sublethal physiological effects and metal residue accumulation in tissues were measured in adult and juvenile rainbow trout fed a metal-contaminated diet and/or exposed to waterborne metals for 21 d. The consumption of metal-contaminated invertebrates from the Clark Fork River, Montana, significantly affected scale loss and metal accumulation in gut tissue of adult trout. Survival, scale loss, and metal accumulation in gill and kidney tissue were affected by exposure to a waterborne mixture of Cd, Cu, and Pb at twice the acceptable levels and Zn at the maximum acceptable level established by the U.S. Environmental Protection Agency for protection of aquatic wildlife. A combination of dietary and waterborne metals also caused lipid peroxidation in the kidney of adult fish and decreased whole-body potassium of juvenile trout. In general, metal accumulation in tissues was higher in gill and kidney with waterborne exposures and was higher in stomach and pyloric caeca with dietary exposure. And metal concentrations in juvenile whole-body tissues accumulated significantly with a combination of waterborne and dietary metals. Although some physiological changes were noted (scale loss, lipid peroxidation of kidney), an exposure time longer than 21 d is probably needed to observe more extensive physiological changes. Regardless, results from this study suggest that a full assessment of metal exposure to fish populations in natural systems must include evaluation of dietary as well as waterborne metal contamination.

1552-8618/asset/olbannerleft.gif?v=1&s=27ff872c6376061529ca080147e2f8fb8fdbcad4)
1552-8618/asset/olbannerright.gif?v=1&s=963f2820acff318b2289658b893e9f78f3bd2c1f)
1552-8618/asset/cover.gif?v=1&s=f358d8623a91e6461314c56d177604eeef179c43)