Centre for Ecology and Hydrology, Maclean Building, Benson Lane, Wallingford Oxfordshire OX10 8BB, UK; Institute of Environmental Sciences, University of Leiden, P.O. Box 9518, 2300 RA Leiden, the Netherlands.
Institute of Environmental Sciences, University of Leiden, P.O. Box 9518, 2300 RA Leiden, the Netherlands.
Ecotoxicol Environ Saf. 2018 Dec 30;166:26-34. doi: 10.1016/j.ecoenv.2018.09.052. Epub 2018 Sep 19.
Daphnia magna were exposed to two pesticides in the presence or absence of microplastics (300 000 particles ml 1 µm polystyrene spheres) and to microplastics alone. The pesticides were dimethoate, an organophosphate insecticide with a low log Kow, and deltamethrin, a pyrethroid insecticide with a high log Kow. Daphnia were exposed to a nominal concentration range of 0.15, 0.31, 0.63, 1.25, 2.5, 5 mg l dimethoate and 0.016, 0.08, 0.4, 2, 5 and 10 µg l deltamethrin. Exposure to polystyrene microplastics alone showed no effects on Daphnia magna survival and mobility over a 72 h exposure. In the dimethoate exposures, mobility and survival were both affected from a concentration of 1.25 mg l, with effects were seen on mobility from 28 h and survival from 48 h, with greater effects seen with increasing concentration and exposure time. In deltamethrin exposures, survival was affected from a concentration of 0.4 µg l and mobility from a concentration of 0.08 µg l. Effects of deltamethrin on mobility were seen from 5 h and on survival from 28 h, with greater effects on survival and mobility seen with increasing concentration and exposure time. Contrary to expectations, pesticide toxicity to Daphnia magna was not affected by the presence of microplastics, regardless of chemical binding affinity (log Kow). This therefore suggests that polystyrene microplastics are unlikely to act as a significant sink, nor as a vector for increased uptake of pesticides by aquatic organisms. CAPSULE: Polystyrene microplastics are unlikely to act as vector for increased uptake of pesticides by aquatic organisms.
大型溞在存在或不存在微塑料(300000 个粒子 ml 1μm 聚苯乙烯球)和单独存在微塑料的情况下暴露于两种农药中。这两种农药是甲拌磷,一种具有低 log Kow 的有机磷杀虫剂,和溴氰菊酯,一种具有高 log Kow 的拟除虫菊酯杀虫剂。大型溞暴露于 0.15、0.31、0.63、1.25、2.5 和 5mg/L 甲拌磷和 0.016、0.08、0.4、2、5 和 10μg/L 溴氰菊酯的名义浓度范围内。单独暴露于聚苯乙烯微塑料在 72 小时暴露期间对大型溞的生存和活动能力没有影响。在甲拌磷暴露中,从 1.25mg/L 的浓度开始,活动能力和生存能力都受到影响,从 28 小时开始出现活动能力的影响,从 48 小时开始出现生存能力的影响,随着浓度和暴露时间的增加,影响更大。在溴氰菊酯暴露中,从 0.4μg/L 的浓度开始影响生存能力,从 0.08μg/L 的浓度开始影响活动能力。溴氰菊酯对活动能力的影响从 5 小时开始,对生存能力的影响从 28 小时开始,随着浓度和暴露时间的增加,对生存能力和活动能力的影响更大。与预期相反,无论化学结合亲和力(log Kow)如何,微塑料的存在都不会影响大型溞对农药的毒性。因此,这表明聚苯乙烯微塑料不太可能作为增加水生生物对农药吸收的重要汇,也不太可能作为载体。