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Endocrine activity in the aquatic environment - Establishment of a bioassay battery to detect endocrine disruptive substances in various sample matrices

机译:水生环境中的内分泌活动-建立生物测定电池组以检测各种样品基质中的内分泌破坏性物质

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摘要

Earth’s accessible freshwater resources are under constant pressure. Most of the 35 million cubic kilometers freshwater are bound in glaciers (over 68 %), permanent snow und not accessible groundwater resources. Accessible freshwater is crucial for mankind as well as ecosystems functions in general. At the same time, over 50 % of all renewable and accessible freshwater flows are already used by mankind. In Europe only 21 % of the available freshwater are used and most of it is not consumed but restored. Therefore, Europe’s problems related to freshwater supply do not depend on absolute quantity but on distribution, alterations of the hydromorpholgy and an increasing number of (anthropogenic) pollutants. Because of their potential to disrupt the reproduction over altering the endocrine system one important and heavy discussed group of micropollutants are the endocrine disruptive compounds (EDCs). In the last years more and more (potential) EDCs have been detected in the environment as well as organic tissues of humans and wildlife. For the prediction of a substance’s endocrine activity a first screening with QSAR tools (e.g. OECD QSAR Toolbox, VirtualToxLab) is useful. These predictions actually are good in case of receptor binding properties if the chemical structure is known. To screen samples for known EDCs, chemical analysis is a fast and sensitive approach. For example, to date it is possible to detect estrogens in the low ng∙L-1 range (e.g. 0.3 ng∙L-1 17ß-Estradiol) in groundwater samples with a LC system coupled to a triple-stage quadrupole mass spectrometer with electrospray ion source (LC-ESI-MS2). Nevertheless, to detect unknown endocrine disruptive potentials of a substance or to screen an environmental sample with unknown composition, bioassays are the methods of choice. In the present study, the two recombinant receptor-reporter assays lyticase assisted yeast estrogen screen (LYES) and “estrogen receptor mediated chemical activated luciferase gene expression” (ER CALUX®) assay as well as the H295R steroidogenesis assay, that allows the detection of effects on the whole steroid synthesis pathway, were applied. Additionally, a variation of the in vivo reproduction test with the New Zealand mudsnail Potamopyrgus antipodarum (Pa-Repro) has been used. This bioassay battery therefore covers receptor-mediated activities as well as activities on the process of steroid genesis and impacts on whole organisms as well as populations. To get insights into the development as well as international validation of knew test systems for the detection of EDCs the validation of the newly developed H295R was scientifically attended. It could be shown that the H295R successfully detected all suspected or known EDCs with good correlations between the different laboratories. Nevertheless, beside the number of advantages of this test system some disadvantages were also figured. Those were the high variability of steroid concentration between different passages as well as the high costs for the detection of produced steroids. To overcome the disadvantages several approaches to improve the test system were pursued. At first cells were adapted to chemical defined media which lead to a more stable production of steroids. With the development of a new ELISA method for the detection of steroids in the exposure medium both costs as well as working time could be saved. Hereafter, the selected bioassay battery was applied to various sample matrices as well as single substances. Both LYES and ER CALUX® were used to assess the estrogenic activity of heterocyclic aromatic hydrocarbons (hetero-PAHs). While none of the hetero-PAHs showed estrogenicity in the LYES, nine (indole, 1 benzothiophene, benzofuran, 2-methylbenzofuran, 2,3-dimethylbenzofuran, quinoline, 6 methylquinoline, carbazole, dibenzothiophene, dibenzofuran, acridine, and xanthene) out of twelve showed significant estrogenic activity in the ER CALUX®. With the help of liquid chromatography with diode array detection (LC-DAD) and high resolution tandem mass spectrometry (LC-HRMS2), it could be demonstrated that the used T47Dluc cell line was capable for metabolizing of the parent substances. To assess the endocrine disrupting potential of the biological larvicide VectoBac®, which is extracted out of Bacillus thuringienses var. israelensis (Bti), the whole bioassay battery was used. With both receptor-mediated assays LYES and ER CALUX® the previously detected estrogenic activity of three commercial available tablet formulas could be confirmed. From the subsequently investigated active substance VectoBac® TP as well as the formula WDG only TP showed dose-dependent estrogenic activity in both assays. Neither for TP nor WDG clear influences on the steroidogenesis could be detected in the H295R. The investigation of surface and groundwater samples which were taken after the application of both TP and WDG also showed no estrogenic activity in the receptor-mediated bioassays. To elucidate the potential effect of the suspected xenoestrogen VectoBac® TP on a complex aquatic community a microcosm study was performed. Within this microcosm, the impact on phytoplankton and zooplankton as well as the grazer P. antipodarum could be studied. While no effects on the zooplankton were detected, a clear shift from green to blue algae could be detected at concentrations which also showed significant estrogenic activity in the LYES. No clear effects on the reproduction of P. antipodarum could be observed, but it is assumed that this was a result of the limited food supply due to the community shift within the phytoplankton. Nevertheless, the concentrations used in the microcosm study were ten to 50 times higher than it would be expected in the field and therefore, a shift in the ecosystem structure of routinely treated areas seems unlikely. In the last approach the three selected in vitro bioassays were used to assess the performance of advanced sewage treatment processes with regard to the removal of pharmaceuticals from hospital sewage before discharge into the public sewerage. The high estrogenic activity of the raw sewage sample detected in the LYES could be significantly reduced by a full scale membrane bioreactor (MBR). After subsequent ozonation the estrogenicity was reduced to the level of the solvent controls in both receptor-mediated assays. By means of liquid chromatography-tandem mass spectrometry (LC-MS2) it could be verified that after ozonation concentrations of estrone (E1) were significantly reduced. In contrast, there was a significant increase of 17ß-estradiol production as well as aromatase activity in H295R cells after ozonation. It is hypothesized that this is partly due to formation of active by-products during ozonation. Overall, the selected in vitro bioassays were suitable for the detection of endocrine activity in various sample matrices as well as single substances. The receptor-mediated bioassay ER CALUX® was able to detect estrogenic activity in all matrices used. These included groundwater, surface water and sewage as well as single substances (hetero-PAHs). Additionally, in case of the hetero-PAHs, the estrogenic activity of single substances which require metabolic activation could be detected. With the LYES investigation of medium to highly contaminated water samples was possible, low contaminated water samples could not be investigated due to the high limit of detection (LOD) as well as the relatively high estrogenicity of the solvent controls. The H295R was applicable for medium contaminated samples as well as single substances. Performance of the bioassays markedly varied throughout the present study. The ER CALUX® provided the most stable performance (very good), followed by the H295R (good), the LYES (good to moderate) and P. antipodarum (moderate). Problems occurred with the consistent production of testosterone (H295R), the background of the solvent controls (LYES) as well as food supply and response to the positive control (P. antipodarum). Concluding, it can be stated that the selected bioassay battery is suitable to detect (potential) endocrine disrupting substances in different water sample matrices such as groundwater, surface water and wastewater. Additionally, even single substances that require metabolic activation to exert their estrogenic activity can be investigated.
机译:地球上可获得的淡水资源一直处于压力之下。在3500万立方公里的淡水中,大部分被冰川约束(超过68%),永久性积雪和不可获取的地下水资源。可获得的淡水对于人类以及整个生态系统的功能至关重要。同时,人类已经使用了超过50%的可再生和可利用的淡水流量。在欧洲,仅使用了21%的可用淡水,大部分淡水没有被消耗而是被恢复。因此,欧洲与淡水供应有关的问题不取决于绝对数量,而取决于分布,形态学的改变和(人为)污染物的增加。由于它们有可能通过改变内分泌系统破坏繁殖,因此,一组重要且讨论最多的微污染物是内分泌破坏性化合物(EDC)。近年来,在环境以及人类和野生生物的有机组织中发现了越来越多的(潜在)EDC。为了预测物质的内分泌活性,首先使用QSAR工具(例如OECD QSAR Toolbox,VirtualToxLab)进行筛选是很有用的。如果化学结构已知,这些预测在受体结合特性的情况下实际上是好的。为了筛选样品中已知的EDC,化学分析是一种快速而敏感的方法。例如,迄今为止,通过液相色谱系统与电喷雾三级四极质谱仪联用的液相色谱系统,可以检测地下水样品中低ng∙L-1范围内的雌激素(例如0.3 ng∙L-117ß-雌二醇)。离子源(LC-ESI-MS2)。然而,要检测某种物质的未知内分泌破坏潜能或筛选成分未知的环境样品,生物测定是首选方法。在本研究中,两种重组受体-报告测定法裂解酶辅助酵母雌激素筛选(LYES)和“雌激素受体介导的化学激活的萤光素酶基因表达”(ERCALUX®)测定法以及H295R类固醇生成测定法,可检测应用了对整个类固醇合成途径的影响。另外,已经使用了用新西兰泥指甲波莫氏草(Potamopyrgus antipodarum)(Pa-Repro)进行的体内生殖测试的变体。因此,该生物测定电池涵盖了受体介导的活性以及类固醇生成过程中的活性以及对整个生物体和种群的影响。为了深入了解已知的用于检测EDC的测试系统的开发以及对它们的国际验证,科学地参与了最新开发的H295R的验证。可以证明,H295R成功地检测了所有可疑或已知的EDC,并且在不同实验室之间具有良好的相关性。然而,除了该测试系统的许多优点之外,还发现了一些缺点。这些是不同传代之间类固醇浓度的高变异性以及检测产生的类固醇的高成本。为了克服这些缺点,人们寻求了几种改进测试系统的方法。起初,细胞适应了化学成分确定的培养基,从而导致类固醇的产生更加稳定。通过开发一种新的ELISA方法来检测暴露介质中的类固醇,可以节省成本和工作时间。此后,将所选的生物测定电池应用于各种样品基质以及单一物质。 LYES和ERCALUX®均用于评估杂环芳烃(杂多环芳烃)的雌激素活性。尽管杂多环芳烃均未在LYES中显示出雌激素性,但其中有九种(吲哚,1个苯并噻吩,苯并呋喃,2-甲基苯并呋喃,2,3-二甲基苯并呋喃,喹啉,6个甲基喹啉,咔唑,二苯并噻吩,二苯并呋喃,a啶和x吨)十二个在ERCALUX®中显示出明显的雌激素活性。借助带二极管阵列检测的液相色谱(LC-DAD)和高分辨率串联质谱(LC-HRMS2),可以证明使用的T47Dluc细胞系能够代谢母体物质。为了评估从苏云金芽孢杆菌中提取的生物杀幼虫剂VectoBac®的内分泌破坏潜力。以色列(Bti),整个生物测定电池都用完了。通过两种受体介导的测定法LYES和ERCALUX®,可以确认先前检测到的三种市售片剂的雌激素活性。从随后研究的活性物质VectoBac®TP以及WDG配方中,只有TP在两种测定中均显示出剂量依赖性雌激素活性。对于TP和WDG,在H295R中均未检测到对类固醇生成的明显影响。在同时施用TP和WDG后对地表和地下水样品进行的调查也显示在受体介导的生物测定中没有雌激素活性。为了阐明异种雌激素VectoBac®TP对复杂水生群落的潜在影响,进行了微观研究。在这个缩影中,可以研究对浮游植物和浮游动物以及放牧者抗疟原虫的影响。虽然未检测到对浮游动物的影响,但在LYES中也显示出明显的雌激素活性的浓度下,可以检测到从绿藻到蓝藻的明显转变。没有观察到对P. antipodarum繁殖有明显影响,但是可以认为这是由于浮游植物内部的群落转移而导致食物供应有限的结果。然而,微观研究中使用的浓度比现场预期的浓度高10至50倍,因此,常规处理地区的生态系统结构似乎不太可能发生变化。在最后一种方法中,使用了三种选择的体外生物测定法来评估先进污水处理工艺在排入公共污水之前从医院污水中去除药物方面的性能。在LYES中检测到的原污水样品的高雌激素活性可通过全尺寸膜生物反应器(MBR)大大降低。在随后的臭氧化之后,在两种受体介导的测定中,雌激素性均降低至溶剂对照的水平。通过液相色谱-串联质谱法(LC-MS2),可以证实臭氧化后雌酮(E1)的浓度显着降低。相比之下,臭氧化后H295R细胞中17β-雌二醇的产生以及芳香酶的活性显着增加。假设这部分是由于在臭氧化过程中形成了活性副产物。总体而言,所选的体外生物测定法适用于检测各种样品基质以及单一物质中的内分泌活性。受体介导的生物测定法ERCALUX®能够检测所有所用基质中的雌激素活性。其中包括地下水,地表水和污水以及单一物质(杂多环芳烃)。另外,在杂PAHs的情况下,可以检测到需要代谢活化的单一物质的雌激素活性。通过LYES可以对中度至高度污染的水样品进行调查,由于检测限(LOD)较高以及溶剂对照的雌激素含量较高,因此无法对低污染的水样品进行调查。 H295R适用于中等污染的样品以及单一物质。在整个本研究中,生物测定的性能明显不同。 ERCALUX®提供了最稳定的性能(非常好),其次是H295R(良好),LYES(中等至中等)和抗疟原虫(中等)。持续产生睾丸激素(H295R),溶剂对照的背景(LYES)以及食物供应和对阳性对照(P. antipodarum)的反应均出现问题。总之,可以说所选的生物测定电池适合于检测不同水样基质中的(潜在的)内分泌干扰物质,例如地下水,地表水和废水。另外,甚至可以研究需要代谢激活才能发挥其雌激素活性的单一物质。

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    Maletz Sibylle Xenia;

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  • 年度 2015
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