Abstract:Two recirculated marine seawater systems (capacities: 150 and 300 1) were used for the study on cadmium accumulation of biological filter sludge, by the mussel Mytilus edulis and the plaice Pleuronectes platessa for a period of up to 300 days. In the contaminated system Cd concentrations varied from 2.5 to 7.0 #g/1 with a mean of 4.6 + 1.15 #g/1 (control: 1.04 + 0.46 #g/l). Accumulation of Cd by the filter sludge from the control system as well as from the contaminated system was significant. Mean concentratio… Show more
“…Many of these signs of ascorbic acid deficiency are also characteristic of cadmium poisoning. The growth rate decreases, anaemia and haemorrhages develop, fin regeneration is delayed, and the skeleton becomes deformed in cadmium intoxicated fish (Cearley & Coleman, 1974;Larsson, 1975;Weis & Weis, 1976;Westernhagen et al, 1978Westernhagen et al, , 1980. Hepatic cytochrome P-450 levels fall in rats exposed to cadmium (Schnell et al, 1979) and also in scorbutic guinea pigs (Omaye & Turnbull, 1979).…”
Section: Discussionmentioning
confidence: 99%
“…fBattelle New England Laboratories, 397 Washington St., Duxbury, MA 02332, U.S.A. I83 0022-1 112/82/020183+14 $02.00/0 signs of cadmium poisoning are also found in fish. Decreased growth rates (Westernhagen et al, 1978), lowered blood iron and calcium concentrations (Larsson, 1975;Roch & Maly, 1979) and testicular injury (Sangalang & O'Halloran, 1972) in fish have been reported after cadmium exposure. However, there is little published work on the interrelationship between ascorbic acid status and cadmium toxicity in teleosts.…”
The effects of acute and chronic cadmium exposures on ascorbic acid concentrations and cadmium accumulation in the tissues of juvenile mullet, Mugil cephalus, are described. Hepatic ascorbic acid reserves were maintained in untreated mullet fed a diet containing ascorbate, but decreased 60% in individuals exposed to 10 mg Cd I-' for six weeks. Ascorbic acid depletion was accompanied by a massive accumulation of cadmium in the liver. Similar changes were found in gill tissue. In contrast, ascorbic acid concentrations were largely unaffected in kidney tissue which had a limited capacity to accumulate the metal. There were marked fluctuations of ascorbic acid levels in the brain. Only small amounts of cadmium were accumulated by this tissue. These results indicate that in mullet liver, gill and brain ascorbic acid stores may be depleted during chronic cadmium poisoning.
“…Many of these signs of ascorbic acid deficiency are also characteristic of cadmium poisoning. The growth rate decreases, anaemia and haemorrhages develop, fin regeneration is delayed, and the skeleton becomes deformed in cadmium intoxicated fish (Cearley & Coleman, 1974;Larsson, 1975;Weis & Weis, 1976;Westernhagen et al, 1978Westernhagen et al, , 1980. Hepatic cytochrome P-450 levels fall in rats exposed to cadmium (Schnell et al, 1979) and also in scorbutic guinea pigs (Omaye & Turnbull, 1979).…”
Section: Discussionmentioning
confidence: 99%
“…fBattelle New England Laboratories, 397 Washington St., Duxbury, MA 02332, U.S.A. I83 0022-1 112/82/020183+14 $02.00/0 signs of cadmium poisoning are also found in fish. Decreased growth rates (Westernhagen et al, 1978), lowered blood iron and calcium concentrations (Larsson, 1975;Roch & Maly, 1979) and testicular injury (Sangalang & O'Halloran, 1972) in fish have been reported after cadmium exposure. However, there is little published work on the interrelationship between ascorbic acid status and cadmium toxicity in teleosts.…”
The effects of acute and chronic cadmium exposures on ascorbic acid concentrations and cadmium accumulation in the tissues of juvenile mullet, Mugil cephalus, are described. Hepatic ascorbic acid reserves were maintained in untreated mullet fed a diet containing ascorbate, but decreased 60% in individuals exposed to 10 mg Cd I-' for six weeks. Ascorbic acid depletion was accompanied by a massive accumulation of cadmium in the liver. Similar changes were found in gill tissue. In contrast, ascorbic acid concentrations were largely unaffected in kidney tissue which had a limited capacity to accumulate the metal. There were marked fluctuations of ascorbic acid levels in the brain. Only small amounts of cadmium were accumulated by this tissue. These results indicate that in mullet liver, gill and brain ascorbic acid stores may be depleted during chronic cadmium poisoning.
“…Of all these, mussels are known to be the most sensitive indicators to elevated concentrations of heavy metals, particularly cadmium. Within the food-chain mussels, and to a lesser extent cockles, accumulate high levels or certain heavy metals (von Westernhagen et al 1978, Buchwald et al 1985. These and other diets of waders and shorebirds are contaminated with heavy metals (Packer et al 1970, Evans & Moon 1981, Zunk 1988.…”
“…In vertebrates and invertebrates, effects of Cd on growth (Stebbing, 1976~ Paffenh6fer, 1978yon Westernhagen et al, 1978;Stebbing & Hiby, 1979), embryo and larval development (Calabrese et al, 1973;Mirkes et al, 1978;Reish &Carr, 1978;Alderdice et al, 1979;KI6ckner, 1979;Lehnberg & Theede, 1979), and the alteration of various physiological functions (e. g. osmoregulation, excretion, respiration) (MacInnes & Thurberg, 1973;Thurberg et al, 1973;Dawson et al, 1977;Thurberg et al, 1977) and behaviour (Martin et al, 1975;Eldon & Kristoffersson, 1978) have been observed.…”
Toxic effects of cadmium contamination may be observed at all levels of organismic organization. In estuarine areas the sensitivity of euryhaline species to acute Cd toxicity is strongly modified by various abiotic factors, whereas long-term threshold values are less dependent on environmental parameters. Experiments with larval stages of the mollusc Mytilus edulis reveal that Cd effects on life functions such as development and growth are differentially modified by temperature and salinity. High Cd concentrations can be accumulated by adult bivaives of coastal areas without signs of physiological damage. Mechanisms of heavy-metal detoxication in these molluscs seem to be quite different from those known to exist in vertebrates. Among decapod crustaceans, stenoecous species tend to exhibit higher rates of Cd uptake than euryoecous ones.Rates of Cd uptake and of accumulation depend on external and internal factors. In adult Nereis succinea individuals sublethal Cd effects have been recorded on growth and food conversion (in terms of energy content).
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