Castaño Argelia, Becerril Concepción
CISA INIA. E-28130, Madrid, Spain.
Mutat Res. 2004 Aug 18;552(1-2):141-51. doi: 10.1016/j.mrfmmm.2004.06.010.
Genotoxins present in the aquatic environment are often associated with the decline or disappearance of many wild populations. The hazard assessment of chemicals requires sensitive and specific tests to study the genotoxic effects in order to establish the maximum allowable chemical concentrations prior to the release to the environment. We have previously shown that an established fish cell line (RTG-2) together with the random amplified polymorphic DNA (RAPD) technique, can be used to detect alterations in the DNA caused by direct acting genotoxins. The current study takes this a step further and examines in the same system the effect of a pro-mutagen benzo(a)pyrene (B(a)P) at different concentrations (0.05, 0.1, and 0.5 microg/ml) and at different exposure periods (1, 2, 3, 15, and 30 days). After comparing DNA fingerprints from control and exposed cells, both qualitative and quantitative analysis show an increase in the instability in the DNA fingerprint of exposed cells over a time- and concentration-dependent manner. At the higher concentration (0.5 microg/ml) three out the four primers showed altered bands after 1 day of exposure, while after 3 days all used primers showed an altered pattern. At the lower concentration of B(a)P (0.05 microg/ml) the appearance of new bands was observed with a 100% level of reproducibility after 30 days of exposure suggesting an inheritance of the altered DNA. We conclude that this in vitro system is useful to evaluate genotoxic effects, both after acute and chronic exposures and of direct and non-direct acting genotoxins. Cultured cells can be considered as genetically homogenous populations. Therefore, in vitro systems permits us to undertake mechanistic studies avoiding the interference of polymorphisms inherent in the in vivo systems. Furthermore, the RTG-2 fish cell line combined with a RAPD assay could be used in studies of hazard identification in risk assessment protocols of chemicals.
水生环境中存在的基因毒素通常与许多野生种群的减少或消失有关。化学品的危害评估需要灵敏且特异的测试来研究基因毒性效应,以便在向环境中释放之前确定最大允许化学浓度。我们之前已经表明,一种已建立的鱼类细胞系(RTG - 2)与随机扩增多态性DNA(RAPD)技术相结合,可用于检测由直接作用的基因毒素引起的DNA改变。当前的研究更进一步,在同一系统中检测了前诱变剂苯并(a)芘(B(a)P)在不同浓度(0.05、0.1和0.5微克/毫升)以及不同暴露时间(1、2、3、15和30天)下的效应。在比较对照细胞和暴露细胞的DNA指纹图谱后,定性和定量分析均表明,暴露细胞的DNA指纹图谱不稳定性呈时间和浓度依赖性增加。在较高浓度(0.5微克/毫升)下,暴露1天后,四个引物中有三个显示条带改变,而暴露3天后,所有使用的引物都显示出改变的模式。在较低浓度的B(a)P(0.05微克/毫升)下,暴露30天后观察到新条带的出现,且重现性达100%,这表明改变的DNA具有遗传性。我们得出结论,该体外系统可用于评估急性和慢性暴露后直接和非直接作用的基因毒素的基因毒性效应。培养的细胞可被视为基因同质群体。因此,体外系统使我们能够进行机制研究,避免体内系统中固有多态性的干扰。此外,RTG - 2鱼类细胞系与RAPD分析相结合,可用于化学品风险评估方案中的危害识别研究。