Abstract

Abstract Freshwater unionid mussels, Anodonta grandis grandis, were exposed in the laboratory to nominal [Cd] of 0, 5, 10, 20 and 50 ug/L to determine: 1) whether this species produces metallothionein (MT) in response to Cd exposure, 2) which body parts are involved in the production, and 3) the dose-response relationship between (MT] in body parts and the treatment [Cd] in the laboratory compared with that in a field population exposed to Cd. Background [MT], as µg MT/g wet weight, measured in mussels freshly collected from a pristine lake were: kidney, 38.9 > visceral mass, 15.0; foot, 13.7; gill, 12.5 > mantle, 3.4. After these mussels were exposed to Cd in the laboratory for 22 days, blood [Cd] in the 5–50 µg/L Cd exposures averaged 5.1, 7.1, 9.3 and 15.8 times, respectively, the blood [Cd] in the 0 µg/L treatment. After the 22-day exposure, only [MT] in gill showed a statistically significant relationship with treatment [Cd] indicating that MT was induced in response to Cd exposure. The [MT] in gill after 22 days exposure to 50 µg/L Cd was 24.2 µg/g, 72% higher than in mussels exposed for this period to 0 µg/L Cd. In comparison, [MT] in the gill of mussels collected from a whole lake receiving experimental additions of Cd over three ice-free seasons (epilimnetic means of 0.08, 0.05 and 0.1 µg/L Cd, respectively), was 36.5 ug/g after two seasons exposure and 35.0 µg/g after three seasons, indicating a many-fold greater response to water-borne Cd in the field compared with the laboratory. The other body parts in the mussels collected after three seasons in the Cd-treated lake also contained significantly greater [MT] (kidney, 118.3 µg MT/g; visceral mass, 36.3; foot, 26.0 and mantle, 9.5) than did those from the pristine lake. The field samples thus indicate that all these body parts produce MT in response to exposure to Cd.

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