Toxicology of Aquatic Pollution: Physiological, Molecular by E. W. Taylor

By E. W. Taylor

Whilst this publication was once first released in 1996, the toxins of the earth's freshwater habitats was once, because it is now, an issue of significant obstacle. This synthesis considers the results of pollution on aquatic animals through a chain of study and overview articles that current experimental facts of sublethal and deadly results of more than a few toxicants on the physiological, mobile and subcellular degrees, and that discover innovations for detection of pollutants harm. subject matters coated contain routes of uptake of toxicants; the impression of acute and persistent publicity to poisonous steel ions, really zinc, copper and aluminium, with emphasis at the mechanisms of toxicity and responses to power publicity to sublethal degrees; the influence on fish biology of 2 chemical substances of present obstacle, nitrites and polyaromatic hydrocarbons, that could act as oestrogenic ingredients or effective mutagens; and in vitro experiences of the mechanisms of toxicity on the mobile and subcellular point, together with harm of DNA, utilizing cultured fish cells.

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By E. W. Taylor

Whilst this publication was once first released in 1996, the toxins of the earth's freshwater habitats was once, because it is now, an issue of significant obstacle. This synthesis considers the results of pollution on aquatic animals through a chain of study and overview articles that current experimental facts of sublethal and deadly results of more than a few toxicants on the physiological, mobile and subcellular degrees, and that discover innovations for detection of pollutants harm. subject matters coated contain routes of uptake of toxicants; the impression of acute and persistent publicity to poisonous steel ions, really zinc, copper and aluminium, with emphasis at the mechanisms of toxicity and responses to power publicity to sublethal degrees; the influence on fish biology of 2 chemical substances of present obstacle, nitrites and polyaromatic hydrocarbons, that could act as oestrogenic ingredients or effective mutagens; and in vitro experiences of the mechanisms of toxicity on the mobile and subcellular point, together with harm of DNA, utilizing cultured fish cells.

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Additional info for Toxicology of Aquatic Pollution: Physiological, Molecular and Cellular Approaches (Society for Experimental Biology Seminar Series)

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The respiratory metabolism and swimming performance of young sockeye salmon. Journal of the Fisheries Research Board of Canada, 21(5), 1183-226. N. C. (1970). Gas exchange in rainbow trout (Salmo gairdneri) with varying blood oxygen capacity. Journal of the Fisheries Research Board of Canada, 27, 1069-85. W. W. (1992). Influence of solubility in lipid on bioconcentration of hydrophobic compounds. Ecotoxicology and Environmental Safety, 23, 260-73. W. (1990). Bioaccumulation of Xenobiotic Compounds.

Veith, G. (1985). Absorption dynamics of organic chemical transport across trout gills as related to octanolwater partition coefficient. Toxicology and Applied Pharmacology, 77, 1-10. B. (1979). Estimating rate constants for the uptake and clearance of chemicals by fish. Environmental Science and Technology, 13(12), 1506-10. B. (1991). Solubility of organic chemicals in octanol, triolein, and cod liver oil and relationships between solubility and partition coefficients. Water Research, 25(12), 1515-21.

1987). Fish are able to retain a third to a half of the absorbed Zn. 8% (Hardy & Shearer, 1985; Hardy et al, 1987) and 17-47% in the plaice, Pleuronectes platessa (Milner, 1982). Zinc is an essential trace element and there have been several studies on the nutritional requirements of fish, but there is very little information on the sublethal toxic effects of dietary Zn and no data on acute oral toxicity. Rainbow trout require 15-30 jig g"1 Zn in purified diets, but may need 150 \ig g"1 Zn in foods containing high levels of Ca or P to avoid deficiency (Ogino & Yang, 1978; Ketola, 1979; Hardy & Shearer, 1985).

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