Behrens Daphné, Rouxel Julien, Burgeot Thierry, Akcha Farida
Ifremer, Laboratoire d'Ecotoxicologie, Rue de l'Ile d'Yeu, BP21105, 44311 Nantes, cedex 03, France.
Ifremer, Laboratoire d'Ecotoxicologie, Rue de l'Ile d'Yeu, BP21105, 44311 Nantes, cedex 03, France.
Aquat Toxicol. 2016 Jun;175:249-59. doi: 10.1016/j.aquatox.2016.04.003. Epub 2016 Apr 4.
Herbicides are one of the major classes of pollutants contaminating coastal waters over the world. Among them, diuron (3-(3,4-dichlorophenyl)-1,1-dimethylurea) is a phenylurea herbicide frequently detected in oyster-producing area, known to be toxic for this important exploited non-target species. With the aim to investigate the mechanisms by which diuron displays its toxicity in oyster, the implication of both biotransformation and oxygen reactive species (ROS) production was studied considering embryotoxicity and genotoxicity as endpoints. Comparative embryotoxicity and genotoxicity of diuron and its main metabolites (DCPMU, DCPU and 3,4-DCA) were thus studied on oyster larvae by the embryo-larval bioassay on D larvae and the comet assay on trochophore larvae, respectively. Exposures were also performed in presence and absence of known ROS scavenger compounds - ascorbic acid and N-acetylcysteine, to evaluate the involvement of oxyradicals in the toxic responses. In the case of diuron, the production of ROS on exposed oyster larvae was also measured using 2',7'-dichlorodihydrofluorescein diacetate as a probe for flow cytometric analysis. The results we obtained showed the embryotoxicity and genotoxicity of diuron and its metabolites in early life stages of the Pacific oyster. For concentrations ranging from 0.05 to 0.5μgL(-1), diuron appeared significantly more embryotoxic than DCPMU and DCPU (p<0.001). Embryotoxicity decreased with diuron metabolism as follows: diuron≥DCPMU=DCPU, highlighting that biotransformation can constitute a true detoxication pathways in oyster larvae by decreasing the toxicity of the parent compound. In the opposite, no difference was observed between diuron and its metabolites concerning larval development when considering a lower and more environmentally realistic range of concentrations (0.002-0.050μgL(-1)). 3,4-DCA was the only compound that did not show any sign of embryotoxicity, even at concentrations up to 5μgL(-1). Concerning genotoxicity, no significant difference was observed between diuron and all of its metabolites including 3, 4 DCA with damages detected from the concentration of 0.05μgL(-1). As for diuron, the toxicity of the metabolites seems to be mediated in some part by ROS production as clearly demonstrated by the decrease in genotoxicity and developmental abnormalities in the presence of the oxidant scavenger, ascorbic acid.
除草剂是污染全球沿海水域的主要污染物类别之一。其中,敌草隆(3-(3,4-二氯苯基)-1,1-二甲基脲)是一种在牡蛎产区经常检测到的苯基脲类除草剂,已知对这种重要的被开发利用的非目标物种有毒。为了研究敌草隆在牡蛎中表现出毒性的机制,以胚胎毒性和遗传毒性为终点,研究了生物转化和活性氧(ROS)产生的影响。因此,分别通过对D型幼虫的胚胎-幼虫生物测定法和对担轮幼虫的彗星试验,研究了敌草隆及其主要代谢产物(DCPMU、DCPU和3,4-DCA)对牡蛎幼虫的比较胚胎毒性和遗传毒性。还在存在和不存在已知的ROS清除剂化合物(抗坏血酸和N-乙酰半胱氨酸)的情况下进行暴露试验,以评估氧自由基在毒性反应中的作用。对于敌草隆,还使用2',7'-二氯二氢荧光素二乙酸酯作为流式细胞术分析的探针,测量了暴露的牡蛎幼虫中ROS的产生。我们获得的结果表明,敌草隆及其代谢产物在太平洋牡蛎的早期生命阶段具有胚胎毒性和遗传毒性。对于浓度范围为0.05至0.5μg/L(-1)的情况,敌草隆的胚胎毒性明显高于DCPMU和DCPU(p<0.001)。随着敌草隆的代谢,胚胎毒性降低如下:敌草隆≥DCPMU = DCPU,突出表明生物转化可以通过降低母体化合物的毒性,在牡蛎幼虫中构成一条真正的解毒途径。相反,当考虑较低且更符合环境实际的浓度范围(0.002 - 0.050μg/L(-1))时,在幼虫发育方面,敌草隆与其代谢产物之间未观察到差异。3,4-DCA是唯一即使在浓度高达5μg/L(-1)时也未显示出任何胚胎毒性迹象的化合物。关于遗传毒性,在敌草隆与其所有代谢产物(包括3,4-DCA)之间未观察到显著差异,在浓度为0.05μg/L(-1)时检测到损伤。至于敌草隆,代谢产物的毒性似乎在一定程度上由ROS的产生介导,正如在存在抗氧化剂抗坏血酸的情况下遗传毒性和发育异常的降低所清楚表明的那样。