Department of Environmental Science, Aarhus University, Roskilde, Denmark.
Mutat Res. 2013 Jan 20;750(1-2):12-8. doi: 10.1016/j.mrgentox.2012.07.006. Epub 2012 Sep 16.
The Ames II bacterial mutagenicity assay is a new version of the standard Ames test for screening chemicals for genotoxic activity. However, the use of plastic micro-titer plates has drawbacks in the case of testing hydrophobic mutagens, since sorptive and other losses make it difficult to control and define the exposure concentrations, and they reduce availability for bacterial uptake or to the S9 enzymes. With passive dosing, a biocompatible polymer such as silicone is loaded with the test compound and acts as a partitioning source. It compensates for any losses and results in stable freely dissolved concentrations. Passive dosing using silicone O-rings was applied in the Ames II assay to measure PAH mutagenicity in strains TA98 and TAMix - a mixture of six different bacterial strains detecting six different base-pair substitutions - after metabolic activation by S9. Initially, 10 PAHs were tested with passive dosing from saturated O-rings, aiming at levels in the test medium close to aqueous solubility. Fluoranthene, pyrene and benzo(a)pyrene were mutagenic in both TA98 and TAMix, whereas benz(a)anthracene was mutagenic in TA98 only. The concentration-dependent mutagenic activity of benzo(a)pyrene was then compared for passive dosing and solvent spiking. With spiking, nominal concentrations greatly exceeded aqueous solubility before mutagenicity was observed, due to sorptive losses and limiting dissolution kinetics. In contrast, the passive dosing concentration-response curves were more reproducible, and shifted towards lower concentrations by several orders of magnitude. This study raises fundamental questions about how to introduce hydrophobic test substances in the Ames II assay with biotransformation, since the measured mutagenicity not only depends on the compound potency but also on its supply, sorption and consumption during the assay.
Ames II 细菌致突变性检测是用于筛选具有遗传毒性的化学物质的标准 Ames 检测的新版本。然而,在测试疏水性诱变剂的情况下,使用塑料微量滴定板有一些缺点,因为吸附和其他损失使得难以控制和定义暴露浓度,并且它们减少了细菌摄取或 S9 酶的可用性。通过被动给药,生物相容的聚合物(如硅酮)可以负载测试化合物,并作为分配源。它可以弥补任何损失,并导致稳定的自由溶解浓度。在 Ames II 检测中,使用硅酮 O 形环进行被动给药,以在 S9 代谢激活后测量 TA98 和 TAMix 菌株(一种混合了六种不同细菌菌株的混合物,可检测六种不同的碱基对替换)中的 PAH 致突变性。最初,用被动给药从饱和 O 形环测试了 10 种 PAH,目的是使测试介质中的浓度接近水溶解度。荧蒽、芘和苯并(a)芘在 TA98 和 TAMix 中均具有致突变性,而苯并(a)蒽仅在 TA98 中具有致突变性。然后比较了苯并(a)芘的被动给药和溶剂加注的浓度依赖性致突变活性。由于吸附损失和有限的溶解动力学,在观察到致突变性之前,溶剂加注的名义浓度大大超过了水溶解度,从而大大超过了水溶解度。相比之下,被动给药的浓度反应曲线更具重现性,并且向低浓度移动了几个数量级。这项研究提出了关于如何在 Ames II 检测中引入具有生物转化的疏水性测试物质的基本问题,因为所测量的致突变性不仅取决于化合物的效力,还取决于其在检测过程中的供应、吸附和消耗。