Enzyme responses and lipid peroxidation in gills and hepatopancreas of clam Mactra vereformis, following cadmium exposure

被引:0
作者
Xiaoyu Wang
Hongsheng Yang
Guangbin Liu
Qing Wang
机构
[1] Chinese Academy of Sciences,Key Laboratory of Marine Ecology and Environmental Sciences, Institute of Oceanology
[2] Tianjin Fisheries Research Institute,undefined
[3] Mariculture Institute of Shandong Province,undefined
来源
Chinese Journal of Oceanology and Limnology | 2011年 / 29卷
关键词
ACP; ALP; antioxidant enzymes; cadmium; MDA;
D O I
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中图分类号
学科分类号
摘要
To assess the toxicity of heavy metal pollution to marine intertidal shellfish, enzymatic responses and lipid peroxidation were investigated in the clam Mactra vereformis exposed to cadmium under laboratory conditions. Three antioxidant enzymes (superoxide dismutase, SOD; catalase, CAT; glutathione peroxidase, GPx), two immune defense enzymes (acid phosphatase, ACP; alkaline phosphatase, ALP), and one lipid peroxidation product (malondialdehyde, MDA) were measured in the gills and the hepatopancreas of the clam exposed to 0, 25, 75, and 125 μg/L cadmium for 0, 1, 3, 5, and 7 d. The results show that the concentrations of antioxidant enzymes in the organs soared to a peak value on the first day and then decreased afterwards in most cases. CAT and GPx activities in the hepatopancreas were higher than in the gills, but the SOD activity was lower in the hepatopancreas. ACP activity was unchanged until Day 3 in the hepatopancreas and until Day 5 in gills, when it began to increase. ALP activity showed no significant relationship with Cd treatment. MDA concentrations increased in the two tissues after Cd exposure, peaked on Day 3 in gills, and on Day 5 in hepatopancreas. These observations show that changes in the activities of antioxidant enzymes and ACP reflect the time course of oxidative stress in the clam caused by Cd, and could be used as potential biomarkers for ecotoxicological bioassays of heavy metals.
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页码:981 / 989
页数:8
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[1]  
Almeida J. A.(2002)The use of the oxidative stress responses as biomarkers in Nile tilapia ( Environ. Int. 27 673-679
[2]  
Diniz Y. S.(2005)) exposed to in vivo cadmium contamination Aquat. Toxicol. 75 354-373
[3]  
Marques S. F. G.(1985)Antioxidant systems and lipid peroxidation in Can. J. Biochem. Cell Biol. 63 1 212-1 216
[4]  
Faine L. A.(1976) from Mid-Atlantic Ridge hydrothermal vent fields Anal. Biochem. 72 248-254
[5]  
Ribas B. O.(1998)Influence of mercury (II), cadmium (II), methylmercury, and phenylmercury on the kinetic properties of rat liver glutathione peroxidase Arch. Biochem. Biophys. 351 257-264
[6]  
Burneiko R. C.(2005)A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding Mar. Inform. 3 20-23
[7]  
Novelli E. L. B.(2004)Biochemical defense mechanisms against copper-induced oxidative damage in the blue crab, Mar. Sci. 28 16-21
[8]  
Bebianno M. J.(2006)Research and demonstration of the technologies of restoring the typical coastal zone tidal-flat habitat and the living resources in the Bohai Sea Mar. Biol. 148 817-825
[9]  
Company R.(1997)An evaluation on heavy metal contamination in the surface sediments in Bohai Sea Ecotoxi. Environ. Safe. 38 122-131
[10]  
Serafim A.(1998)The effect of cadmium on antioxidant responses and the susceptibility to oxidative stress in the hydrothermal vent mussel J. Exp. Biol. 210 1 203-1 209