Sister Chromatid Exchange Test System Research Articles

Antigenotoxic potencies of a lichen species, Evernia prunastri

In this article, the genotoxic and antigenotoxic effects of methanol extract of Evernia prunastri (Huds.) Willd. (MEP) were studied using WP2, Ames (TA1535 and TA1537) and sister chromatid exchange (SCE) test systems. The results obtained from bacterial test systems demonstrated that MEP has strong antimutagenic potencies on TA1537 and WP2 strains. The highest inhibition rates for MEP on TA1537 and WP2 strains were 37.70% and 69.70%, respectively. According to the SCE test system, MEP reduced the genotoxic effects of aflatoxin. In order to clarify the mechanism underlying the antigenotoxic effects of MEP, the antioxidants were determined. Cotreatments of 5, 10 and 20µg/mL concentrations of MEP with aflatoxin B1 decreased the frequencies of SCE and the malondialdehyde level and increased amount of superoxide dismutase, glutathione and glutathione peroxidase which were decreased by aflatoxin. The data obtained from this work have clearly shown that MEP has significant antigenotoxic effects which are thought to be partly due to the antioxidant activities and antioxidant inducing capability of MEP. This is the first report indicating the antigenotoxic activities of MEP against several mutagen agents such as N-methyl-N'-nitro-N-nitrosoguanidine, acridin and aflatoxin.

Effect of 5-bromodeoxyuridine substitution on sister chromatid exchange induction by chemicals

The fluorescence-plus-Giemsa (FPG) technique for analysis of sister chromatid exchange (SCE) is widely used as an assay for mutagenic carcinogens. There is very little information, however, on whether incorporation of the bromodeoxyuridine (BrdU) necessary for visualization of SCEs affects the sensitivity of the SCE test system to different chemical agents. We have investigated the effect of BrdU incorporation on SCE induction by labeling cells with BrdU for either the first cell cycle or the first and second cell cycles. The cells were then treated with bleomycin, which produces DNA strand breakage; proflavine, which intercalates into DNA; mitomycin C, which produces monoadducts and DNA crosslinks; or aphidicolin, which inhibits DNA polymerase alpha. Chemicals were added before BrdU exposure or during the first, second, or both cell cycles. Only mitomycin C, which induces long-lived lesions, elevated the SCE frequency when cells were treated before BrdU labeling. When bleomycin, proflavine, or mitomycin C was present concurrently with BrdU, the frequency of SCEs was increased independently of the BrdU labeling protocol. Aphidicolin, on the other hand, induced more SCEs when present for the second cell cycle, when DNA replicates on a template DNA strand containing BrdU. We also examined the induction of SCEs in the first cell cycle (twins) and in the second cell cycle (singles) after continuous treatment of cells with BrdU and the test chemicals. Only aphidicolin increased SCE frequency in the second cell cycle. These results indicate that aphidicolin, but not bleomycin, proflavine, or mitomycin C, affects BrdU-substituted DNA and unsubstituted DNA differently. This type of interaction should be taken into consideration when the SCE test is used as an assay system.

The SCE test as a tool for cytogenetic monitoring of human exposure to occupational and environmental mutagens.

The sister chromatid exchange (SCE) test system using human peripheral lymphocytes is proposed as a valuable tool for the cytogenetic monitoring of exposure to potential chemical mutagens in the occupational environment. We examined the SCE frequencies in organic solvent-exposed workers and reviewed the effects of occupational and environmental chemicals on SCE frequencies. The results obtained in these exposed populations are rather contradictory, which may be related to confounding factors, such as personal life style (smoking, drinking, and drugs) of the examinees, tissue culture conditions and the number of subjects examined. We discussed some practical problems for exposure estimation and sample size determination and are led to the following conclusions. 1) The possible combined effects of potential mutagens and cigarette smoking should be taken into consideration when using the SCE test system. 2) Cell cycle kinetic analysis by differential chromatid staining would provide valuable information as a biological indicator for the monitoring of the workers exposed to xenobiotics. 3) By appropriately setting the number of examinees, monitoring would become more efficient in detecting an increased SCE frequency in the exposed populations. Further studies are also required to enhance the sensitivity of the SCE test system for monitoring purposes.