Unité de Recherche Hydrosystèmes et Bioprocédés, équipe BELCA, CEMAGREF, Parc de Tourvoie BP 44, Antony, France.
Mutat Res. 2011 Jul 14;723(1):26-35. doi: 10.1016/j.mrgentox.2011.03.008. Epub 2011 Mar 29.
The aim of this study was to assess the genotoxic potential of environmentally relevant concentrations of Cd on the zebra mussel, an important freshwater sentinel organism, and to determine the stability of DNA damage in gill cells and haemocytes. The oxidative DNA damage and the co-genotoxicity of Cd in combination with B[a]P were investigated. We measured DNA damage in haemocytes and gill cells of zebra mussels exposed for 11 days to a constant concentration of Cd (10μg/L), B[a]P (10μg/L) or the two combined chemicals (10μg/L+1μg/L). Enzymatic dissociation of gills with dispase gave the lower percentage DNA in tail, compared with collagenase/dispase or collagenase. Bioaccumulation of cadmium in the soft tissues of mussels exposed to CdCl(2) or CdCl(2)+B[a]P increased in a time-dependent manner indicating that both exposures were effective. Cd (10μg/L) is genotoxic only during the first 3 days of exposure in gill cells, while in haemocytes the genotoxicity of Cd was observed later. B[a]P (10μg/L) induced an early increase of DNA damage in gill cells (after 10h and 1 day), while in both gill cells and haemocytes, B[a]P caused a marked increase of DNA damage after 3 days of exposure. The Cd+B[a]P mixture decreased the DNA-damaging effect of Cd and B[a]P in both cell types. Cd induced an increase of DNA damage in Fpg-treated slides, indicating that Cd contributed to oxidative DNA damage. Cadmium induced a cytogenetic effect in gill cells, assessed by the number of micronuclei, throughout the duration of the exposure, while B[a]P did not induce any cytogenetic effect. B[a]P, Cd and Cd+B[a]P induced a transient increase in the number of bi-nucleated cells. Our data clearly show that gills are more sensitive to Cd and B[a]P, which makes them more suitable for future bio-monitoring studies.
本研究旨在评估环境相关浓度的 Cd 对斑马贻贝(一种重要的淡水指示生物)的遗传毒性,并确定鳃和血细胞中 DNA 损伤的稳定性。研究了 Cd 与 B[a]P 联合作用下的氧化 DNA 损伤和共遗传毒性。我们测量了斑马贻贝血细胞和鳃细胞在持续暴露于 Cd(10μg/L)、B[a]P(10μg/L)或两者联合(10μg/L+1μg/L)11 天后的 DNA 损伤。用Dispase 酶解分离鳃,与胶原酶/ Dispase 或胶原酶相比,尾部的 DNA 百分比更低。暴露于 CdCl2 或 CdCl2+B[a]P 的贻贝软组织中 Cd 的生物积累呈时间依赖性增加,表明两种暴露均有效。Cd(10μg/L)仅在暴露的前 3 天对鳃细胞具有遗传毒性,而在血细胞中,Cd 的遗传毒性则在后期才显现。B[a]P(10μg/L)在 10h 和 1 天后早期增加了鳃细胞的 DNA 损伤,而在鳃细胞和血细胞中,B[a]P 在暴露 3 天后引起了 DNA 损伤的明显增加。Cd+B[a]P 混合物降低了两种细胞类型中 Cd 和 B[a]P 的 DNA 损伤作用。Cd 在 Fpg 处理的载玻片上诱导了 DNA 损伤的增加,表明 Cd 导致了氧化 DNA 损伤。Cd 诱导了暴露期间整个鳃细胞的微核数增加,表明产生了细胞遗传毒性,而 B[a]P 未引起任何细胞遗传毒性。B[a]P、Cd 和 Cd+B[a]P 诱导了双核细胞数量的短暂增加。我们的数据清楚地表明,鳃对 Cd 和 B[a]P 更敏感,这使得它们更适合未来的生物监测研究。