When carp (Cyprinus carpio) were exposed to 5 and 30 ppm Cd in the water, the contents of Cd-binding protein, which has low molecular weight, increased in the hepatopancreas, kidney, gills and gastrointestinal tract with the duration of exposure. This Cd-binding protein was purified from hepatopancreas, kidney, gills, and spleen of carp administered 2 mg/kg Cd (as CdCl2), intraperitoneally for 6 days. Two Cd-binding proteins were separated by DEAE-Sephadex A-25 column chromatography. These proteins had Cd-mercaptide bond, high cysteine contents (ca. 29-34%), but no aromatic amino acids or histidine. From these characteristics the Cd-binding proteins were identified as metallothionein.By using antiserum obtained from a rabbit to which carp hepatopancreas MT-II had been administered, immunological characteristics between hepatopancreas MT-I, II and kidney MT-II were studied, and a slight difference in antigenic determinant was observed among them.By immunological staining techniques with horseradish peroxidase, the localization of metallothionein was investigated. In the nontreated group, metallothionein was present in the acinar cells of hepatopancreas and renal convoluted tubules. In the Cd-treated group (2 mg/kg IP daily for 3 days), metallothionein was present in the nuclei, sinusoids, and extracellular space of hepatopancreas, in addition to the acinar cells. Carp were bred in 1 ppm Cd, 5 ppm Zn solution, and tap water for 14 days, following transfer to 15 ppm Cd solution, respectively. The survival ratio was the highest in the Zn group followed by Cd-treated and control groups. The metallothionein contents increased in hepatopancreas and kidney in the order: Zn>Cd>control group.
IntroductionIt is well known that cadmium-induced renal dysfunction may be the causal substance of Itai-Itai disease. During the 1960s fish kills occurred several times following an increase in water pollution of rivers, lakes and seas in Japan. Some of those were caused by Cd. In Japan the environmental quality standard on water pollution of Cd has been established as <0.01 mg/mL. and since then the characteristics of fish MT separated from eel (5), plaice (6), staghorn sculpin (7), carp (8,9), skipjack (10), rainbow trout (11), and gibel (12) were elucidated.We studied the induction of MT in carp (Cyprinus carpio) exposed to Cd (13), separated MT from carp receiving IP injections of Cd and clarified amino acid compositions and physicochemical characteristics of these proteins (8,9). In addition we examined immunohistological localization of MT in carp organs (14), and the detoxification effect of MT to Cd toxicity (15). This paper summarizes some of the main points.
Experimental and Results
Induction of Cd-Binding ProteinCarp were exposed to 5.30 ppm Cd of in a total volume of 100 L in a polypropylene water tank. Two carp were killed by destruction of the medulla oblongata after 1/3, 1, 4, and 24 hr and 4, 15, and 31 days, and each organ (hepatopancreas, kidney, gill, gastrointestine, spleen, bile, and muscle) were removed. All org...