The University of Queensland, National Research Centre for Environmental Toxicology (Entox), 39 Kessels Rd, Brisbane, Qld 4108, Australia.
Water Res. 2011 Aug;45(14):4238-47. doi: 10.1016/j.watres.2011.05.032. Epub 2011 Jun 7.
A bioanalytical test battery was used for monitoring organic micropollutants across an indirect potable reuse scheme testing sites across the complete water cycle from sewage to drinking water to assess the efficacy of different treatment barriers. The indirect potable reuse scheme consists of seven treatment barriers: (1) source control, (2) wastewater treatment plant, (3) microfiltration, (4) reverse osmosis, (5) advanced oxidation, (6) natural environment in a reservoir and (7) drinking water treatment plant. Bioanalytical results provide complementary information to chemical analysis on the sum of micropollutants acting together in mixtures. Six endpoints targeting the groups of chemicals with modes of toxic action of particular relevance for human and environmental health were included in the evaluation: genotoxicity, estrogenicity (endocrine disruption), neurotoxicity, phytotoxicity, dioxin-like activity and non-specific cell toxicity. The toxicity of water samples was expressed as toxic equivalent concentrations (TEQ), a measure that translates the effect of the mixtures of unknown and potentially unidentified chemicals in a water sample to the effect that a known reference compound would cause. For each bioassay a different representative reference compound was selected. In this study, the TEQ concept was applied for the first time to the umuC test indicative of genotoxicity using 4-nitroquinoline as the reference compound for direct genotoxicity and benzo[a]pyrene for genotoxicity after metabolic activation. The TEQ were observed to decrease across the seven treatment barriers in all six selected bioassays. Each bioassay showed a differentiated picture representative for a different group of chemicals and their mixture effect. The TEQ of the samples across the seven barriers were in the same order of magnitude as seen during previous individual studies in wastewater and advanced water treatment plants and reservoirs. For the first time a benchmarking was performed that allows direct comparison of different treatment technologies and covers several orders of magnitude of TEQ from highly contaminated sewage to drinking water with TEQ close or below the limit of detection. Detection limits of the bioassays were decreased in comparison to earlier studies by optimizing sample preparation and test protocols, and were comparable to or lower than the quantification limits of the routine chemical analysis, which allowed monitoring of the presence and removal of micropollutants post Barrier 2 and in drinking water. The results obtained by bioanalytical tools were reproducible, robust and consistent with previous studies assessing the effectiveness of the wastewater and advanced water treatment plants. The results of this study indicate that bioanalytical results expressed as TEQ are useful to assess removal efficiency of micropollutants throughout all treatment steps of water recycling.
采用生物分析测试组合来监测间接饮用水再利用计划测试点的有机微量污染物,这些测试点涵盖了完整的水循环,从污水到饮用水,以评估不同处理屏障的效果。间接饮用水再利用计划包括七个处理屏障:(1)源头控制,(2)污水处理厂,(3)微滤,(4)反渗透,(5)高级氧化,(6)水库中的自然环境,以及(7)饮用水处理厂。生物分析结果提供了与化学分析相辅相成的信息,反映了混合物中多种微量污染物共同作用的综合效应。在评估中纳入了六个针对对人类和环境健康具有特殊毒性作用模式的化学物质组的终点:遗传毒性、雌激素活性(内分泌干扰)、神经毒性、植物毒性、二恶英样活性和非特异性细胞毒性。水样的毒性以毒性等效浓度 (TEQ) 表示,这是一种将水样中未知和潜在未识别化学物质混合物的效应转化为已知参考化合物所引起的效应的度量。对于每种生物测定,都选择了不同的代表性参考化合物。在这项研究中,TEQ 概念首次应用于指示遗传毒性的 umuC 测试,使用 4-硝基喹啉作为直接遗传毒性的参考化合物,使用苯并[a]芘作为代谢激活后的遗传毒性参考化合物。在所有六个选定的生物测定中,TEQ 随着七个处理屏障的增加而降低。每种生物测定都呈现出不同的化学物质及其混合物效应的特征。水样的 TEQ 在七个屏障之间的顺序与之前在废水和先进水处理厂和水库中的单个研究中观察到的顺序相同。这是首次进行基准测试,允许直接比较不同的处理技术,并涵盖从高度污染的污水到接近或低于检测限的饮用水的几个数量级的 TEQ。通过优化样品制备和测试方案,与早期研究相比,生物测定的检测限降低,与常规化学分析的定量限相当或更低,这允许在屏障 2 之后以及在饮用水中监测微量污染物的存在和去除。生物分析工具获得的结果是可重复的、稳健的,与评估废水和先进水处理厂效果的先前研究一致。本研究的结果表明,以 TEQ 表示的生物分析结果可用于评估整个水循环的水再利用处理步骤中微量污染物的去除效率。