Department of Environmental Biology and Chemistry, Graduate School of Science and Engineering for Research, University of Toyama, Gofuku 3190, Toyama 930-8555, Japan.
Sensors (Basel). 2012 Dec 14;12(12):17414-32. doi: 10.3390/s121217414.
The SOS/umu genotoxicity assay evaluates the primary DNA damage caused by chemicals from the β-galactosidase activity of S. typhimurium. One of the weaknesses of the common umu test system based on spectrophotometric detection is that it is unable to measure samples containing a high concentration of colored dissolved organic matters, sediment, and suspended solids. However, umu tests with electrochemical detection techniques prove to be a better strategy because it causes less interference, enables the analysis of turbid samples and allows detection even in small volumes without loss of sensitivity. Based on this understanding, we aim to develop a new umu test system with hydrodynamic chronoamperometry using a rotating disk electrode (RDE) in a microliter droplet. PAPG when used as a substrate is not electroactive at the potential at which PAP is oxidized to p-quinone imine (PQI), so the current response of chronoamperometry resulting from the oxidation of PAP to PQI is directly proportional to the enzymatic activity of S. typhimurium. This was achieved by performing genotoxicity tests for 2-(2-furyl)-3-(5-nitro-2-furyl)-acrylamide (AF-2) and 2-aminoanthracene (2-AA) as model genotoxic compounds. The results obtained in this study indicated that the signal detection in the genotoxicity assay based on hydrodynamic voltammetry was less influenced by the presence of colored components and sediment particles in the samples when compared to the usual colorimetric signal detection. The influence caused by the presence of humic acids (HAs) and artificial sediment on the genotoxic property of selected model compounds such as 4-nitroquinoline-N-oxide (4-NQO), 3-chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone (MX), 1,8-dinitropyrene (1,8-DNP) and 1-nitropyrene (1-NP) were also investigated. The results showed that the genotoxicity of 1-NP and MX changed in the presence of 10 mg∙L-1 HAs. The genotoxicity of tested chemicals with a high hydrophobicity such as 1,8-DNP and 1-NP were decreased substantially with the presence of 1 g∙L-1 sediment. This was not observed in the case of genotoxins with a low log K(ow) value.
SOS/umu 遗传毒性检测评估了化学物质引起的原发性 DNA 损伤,其检测方法是基于 S. typhimurium 的β-半乳糖苷酶活性来检测。基于分光光度检测的常见umu 测试系统的一个弱点是,它无法测量含有高浓度有色溶解有机物、沉积物和悬浮物的样品。然而,电化学检测技术的 umu 测试被证明是一种更好的策略,因为它引起的干扰较小,能够分析混浊样品,并且可以在不损失灵敏度的情况下检测小体积的样品。基于这一认识,我们旨在开发一种新的 umu 测试系统,该系统使用旋转圆盘电极(RDE)在微升液滴中进行动力chronoamperometry。当 PAPG 用作底物时,在 PAP 被氧化为对醌亚胺(PQI)的电位下没有电化学活性,因此,chronoamperometry 的电流响应直接与 S. typhimurium 的酶活性成正比。这是通过对 2-(2-呋喃基)-3-(5-硝基-2-呋喃基)-丙烯酰胺(AF-2)和 2-氨基蒽(2-AA)等模型遗传毒性化合物进行遗传毒性测试来实现的。本研究结果表明,与常用的比色信号检测相比,基于动力伏安法的遗传毒性检测中,信号检测受样品中有色成分和沉积物颗粒的影响较小。本研究还考察了腐殖酸(HAs)和人工沉积物对所选模型化合物如 4-硝基喹啉-N-氧化物(4-NQO)、3-氯-4-(二氯甲基)-5-羟基-2(5H)-呋喃酮(MX)、1,8-二硝基芘(1,8-DNP)和 1-硝基芘(1-NP)遗传毒性的影响。结果表明,在 10mg∙L-1 HAs 存在的情况下,1-NP 和 MX 的遗传毒性发生了变化。对于疏水性较高的测试化学品,如 1,8-DNP 和 1-NP,在 1g∙L-1 沉积物存在的情况下,其遗传毒性显著降低。而对于 log K(ow) 值较低的遗传毒素,则未观察到这种情况。