Kale Shubha P, Carmichael Mary C, Harris Kelley, Roy-Engel Astrid M
Dept. of Biology, Xavier University of Louisiana, 1 Drexel Dr., New Orleans, LA 70125, USA.
Int J Environ Res Public Health. 2006 Jun;3(2):121-8. doi: 10.3390/ijerph2006030015.
Human exposure to toxic metals is a concern of the highest priority, due to their vast array of biological effects, including carcinogenicity. The particulate (water insoluble) form of several heavy metals presents a higher carcinogenic potential than its soluble counterparts. Our previous work demonstrates that the particulate forms of different heavy metals, such as nickel oxide, cadmium sulfide and mercury sulfide, stimulate human L1 mobile element activity leading to genomic instability. We present data demonstrating that the soluble form of CdCl2 also stimulates L1 retrotransposition in a dose-dependent manner comparable to the insoluble carcinogenic form of this compound. Reproducible results demonstrated a 2 to 3 fold dose-dependent increase in L1 retrotransposition compared to control cells. Heavy metals may cause DNA breaks through the generation of reactive oxygen species. However, evaluation of DNA damage by comet assay revealed no differences between the negative controls and the CdS-treated cells. In addition, active L1 elements express a protein with endonuclease activity that can generate toxicity through the creation of double strand breaks. To determine the contribution of the L1 endonuclease to the toxicity observed in our metal treatment assays, we compared the wildtype L1 vector with an L1 endonuclease-mutant vector. The presence of an active L1 endonuclease did not contribute significantly to the toxicity observed in any of the CdCl2 or CdS doses evaluated. No correlation between the creation of DNA breaks and L1 activity was observed. Alternatively, heavy metals inhibit enzymatic reactions by displacement of cofactors such as Zn and Mg from enzymes. Concomitant treatment with Mg(Ac)2 and Zn(Ac)2 ppb suppresses the stimulatory effect on L1 activity induced by the 3.8 ppb CdS treatment. Overall, these results are consistent with our previous observations, suggesting that the mechanism of L1 stimulation by heavy metals is most likely due to an overall inhibition of DNA repair proteins or other enzymes caused by the displacement of Mg and Zn from cellular proteins.
由于有毒金属具有包括致癌性在内的一系列广泛生物效应,人类接触有毒金属是最优先关注的问题。几种重金属的颗粒(水不溶性)形式比其可溶性对应物具有更高的致癌潜力。我们之前的工作表明,不同重金属的颗粒形式,如氧化镍、硫化镉和硫化汞,会刺激人类L1移动元件活性,导致基因组不稳定。我们提供的数据表明,CdCl2的可溶形式也以剂量依赖的方式刺激L1逆转录转座,其程度与该化合物的不溶性致癌形式相当。可重复的结果表明,与对照细胞相比,L1逆转录转座增加了2至3倍,呈剂量依赖性。重金属可能通过产生活性氧导致DNA断裂。然而,彗星试验对DNA损伤的评估显示,阴性对照和CdS处理的细胞之间没有差异。此外,活跃的L1元件表达一种具有内切核酸酶活性的蛋白质,该蛋白质可通过产生双链断裂产生毒性。为了确定L1内切核酸酶对我们金属处理试验中观察到的毒性的贡献,我们将野生型L1载体与L1内切核酸酶突变载体进行了比较。活性L1内切核酸酶的存在对所评估的任何CdCl2或CdS剂量下观察到的毒性均无显著贡献。未观察到DNA断裂与L1活性之间的相关性。另外,重金属通过从酶中置换锌和镁等辅因子来抑制酶促反应。用Mg(Ac)2和Zn(Ac)2 ppb同时处理可抑制3.8 ppb CdS处理诱导的对L1活性的刺激作用。总体而言,这些结果与我们之前的观察结果一致,表明重金属刺激L1的机制很可能是由于从细胞蛋白质中置换镁和锌导致DNA修复蛋白或其他酶的整体抑制。