Centre for Functional Ecology, Department of Life Sciences, University of Coimbra, Apartado 3046, 3001-401 Coimbra, Portugal.
Environ Int. 2013 Mar;53:18-28. doi: 10.1016/j.envint.2012.12.005. Epub 2013 Jan 8.
The use of pesticides for crop protection may result in the presence of toxic residues in environmental matrices. In the aquatic environment, pesticides might freely dissolve in the water or bind to suspended matter and to the sediments, and might be transferred to the organisms' tissues during bioaccumulation processes, resulting in adverse consequences to non-target species. One such group of synthetic organic pesticides widely used worldwide to combat pathogenic fungi affecting plants is the strobilurin chemical group. Whereas they are designed to control fungal pathogens, their general modes of action are not specific to fungi. Consequently, they can be potentially toxic to a wide range of non-target organisms. The present work had the intent to conduct an extensive literature review to find relevant research on the occurrence, fate and effects of azoxystrobin, the first patent of the strobilurin compounds, in aquatic ecosystems in order to identify strengths and gaps in the scientific database. Analytical procedures and existing legislation and regulations were also assessed. Data gathered in the present review revealed that analytical reference standards for the most relevant environmental metabolites of azoxystrobin are needed. Validated confirmatory methods for complex matrices, like sediment and aquatic organisms' tissues, are very limited. Important knowledge of base-line values of azoxystrobin and its metabolites in natural tropical and estuarine/marine ecosystems is lacking. Moreover, some environmental concentrations of azoxystrobin found in the present review are above the Regulatory Acceptable Concentration (RAC) in what concerns risk to aquatic invertebrates and the No Observed Ecologically Adverse Effect Concentration (NOEAEC) reported for freshwater communities. The present review also showed that there are very few data on azoxystrobin toxicity to different aquatic organisms, especially in what concerns estuarine/marine organisms. Besides, toxicity studies mostly address azoxystrobin and usually neglect the more relevant environmental metabolites. Further work is also required in what concerns effects of exposure to multi-stressors, e.g. pesticide mixtures. Even though Log K(ow) for azoxystrobin and R234886, the main metabolite of azoxystrobin in water, are below 3, the bio-concentration factor and the bioaccumulation potential for azoxystrobin are absent in the literature. Moreover, no single study on bioaccumulation and biomagnification processes was found in the present review.
农药用于作物保护可能导致有毒残留物存在于环境基质中。在水生环境中,农药可能自由溶解在水中或与悬浮物和沉积物结合,并可能在生物累积过程中转移到生物体组织中,从而对非目标物种产生不利影响。在全世界广泛用于防治影响植物的病原真菌的一组合成有机农药是 strobilurin 化学组。虽然它们旨在控制真菌病原体,但它们的一般作用模式并非针对真菌。因此,它们可能对广泛的非目标生物具有潜在毒性。本工作旨在进行广泛的文献综述,以找到有关在水生生态系统中 azoxystrobin(strobilurin 化合物的第一个专利)的发生、命运和影响的相关研究,以确定科学数据库中的优势和差距。还评估了分析程序和现有的立法和法规。本综述中收集的数据表明,需要用于最相关的 azoxystrobin 环境代谢物的分析参考标准。用于复杂基质(如沉积物和水生生物组织)的验证确认方法非常有限。缺乏天然热带和河口/海洋生态系统中 azoxystrobin 及其代谢物的基线值的重要知识。此外,本综述中发现的一些环境浓度的 azoxystrobin 高于水生无脊椎动物的监管可接受浓度 (RAC) 和淡水群落报告的无生态不良影响浓度 (NOEAEC)。本综述还表明,关于 azoxystrobin 对不同水生生物的毒性,特别是对河口/海洋生物的毒性,数据非常少。此外,毒性研究主要涉及 azoxystrobin,通常忽略了更相关的环境代谢物。还需要进一步研究暴露于多胁迫因素(例如农药混合物)的影响。尽管 azoxystrobin 的 Log K(ow) 和 R234886(azoxystrobin 在水中的主要代谢物)低于 3,但文献中缺乏 azoxystrobin 的生物浓缩因子和生物累积潜力。此外,本综述中未发现关于生物累积和生物放大过程的单一研究。