First published online February 1, 2008
Journal of Experimental Biology 211, 577-586 (2008)
Published by The Company of Biologists 2008
doi: 10.1242/jeb.011262
Effects of cadmium on cellular protein and glutathione synthesis and expression of stress proteins in eastern oysters, Crassostrea virginica Gmelin
Anna V. Ivanina*,
Anton S. Cherkasov* and
Inna M. Sokolova
Biology Department, University of North Carolina at Charlotte, 9201
University City Blvd, Charlotte, NC 28223, USA

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Fig. 1. Dose-dependent accumulation of cadmium (Cd) in isolated gill and
hepatopancreas (HP) cells of C. virginica. Mean Cd burdens
(y-axis) accumulated after 4 h exposure in varying Cd concentrations
(x-axis) at 20°C are shown. Vertical bars represent s.e.m.
(N=5).
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Fig. 2. Effects of cadmium (Cd) exposure on protein synthesis rates in gill and
hepatopancreas (HP) cells of oysters. (A, insert) Protein synthesis rates in
control gill and HP cells estimated by the rate of incorporation of
[3H]Leu. Vertical bars represent s.e.m. (N=8). (B) Changes
in [3H]Leu incorporation in response to Cd exposure for 4 h at
20°C expressed as % of the respective controls. Vertical bars represent
s.e.m. Asterisks denote values significantly different from the respective
controls (P<0.05). N=7–8 except for the lowest
(10–25 µmol l–1; N=3) and the highest
(1000–2000 µmol l–1, N=4–5) Cd
levels.
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Fig. 3. Effects of cadmium (Cd) exposure on glutathione synthesis rates in gill and
hepatopancreas (HP) cells of oysters estimated as the rates of
cycloheximide-insensitive incorporation of [3H]Gly. Mean values of
glutathione synthesis in the cells exposed to different Cd levels
(x-axis) for 4 h at 20°C are expressed as % of the respective
controls. Vertical bars represent s.e.m. The asterisk denotes values
significantly different from the respective control [P<0.01; the
dagger denotes a marginally significant difference (P=0.09)].
N=5.
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Fig. 4. Effects of cadmium (Cd) exposure on total glutathione (GSH) concentrations
in gill (A) and hepatopancreas (B) cells of oysters. Cells were incubated for
varying periods of time (x-axis) with 0 µmol l–1
(control) or 2000 µmol l–1 Cd at 20°C, and their total
(reduced + oxidized) GSH levels were determined. P-values for the
effect of Cd on GSH levels, as determined by ANOVA, are given. At each
exposure time, differences in GSH content between control and Cd-exposed cells
were not significant (P>0.05) but the overall effect of Cd
estimated by ANOVA was significant in hepatopancreas cells (see
P-values in the figures). Vertical bars represent s.e.m.
(N=5).
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Fig. 5. Effects of cadmium (Cd) exposure on expression of metallothionein mRNA in
gill and hepatopancreas (HP) cells of oysters. Metallothionein levels were
measured using real-time PCR, normalized to the actin mRNA levels and
expressed as % of the respective controls. Cells were exposed to varying Cd
levels (x-axis) for 4 h at 20°C. (A) mRNA for total
metallothioneins and (B) for metallothionein I only. Vertical bars represent
s.e.m. Asterisks denote values significantly different from the respective
controls (P<0.05). N=9.
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Fig. 6. Effects of cadmium (Cd) exposure on expression of cytoplasmic (HSP70,
HSP90) and mitochondrial (HSP60) heat shock proteins in gill and
hepatopancreas (HP) cells of oysters. HSP levels were measured using
immunoblotting and expressed as % of the respective controls. Cells were
exposed to varying Cd levels (x-axis) for 4 h at 20°C. Vertical
bars represent s.e.m. Asterisks denote values significantly different from the
respective controls (P<0.05). N=5.
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© The Company of Biologists Ltd 2008