Littoral Environnement et Sociétés (LIENSs), UMR 7266, CNRS-Université, de La Rochelle, 2 Rue Olympe de Gouges, F-17042, La Rochelle Cedex 01, France.
Université de Bordeaux, Laboratoire Environnements et Paléoenvironnements Océaniques et Continentaux (EPOC), UMR 5805, F-33600, Pessac, France.
Chemosphere. 2020 Sep;254:126793. doi: 10.1016/j.chemosphere.2020.126793. Epub 2020 Apr 19.
Plastics are persistent synthetic polymers that accumulate as waste in the marine environment. Microplastics (MPs, <5 mm) can be found either as microbeads in body care and some industrial products or as plastic debris through degradation. Plastic microbeads (1-5 μm, fluorescent, Cospheric) were used to characterise the MP ingestion and determine their potential harmful effects on both the swimming behaviour and development of oyster D-larvae (Crassostrea gigas). For 24 h, embryos were first exposed to MPs at a temperature of 24 °C. In addition, 3 day-old D-larvae were exposed to the same temperature for 1, 3 and 5 h. Three concentrations of MPs were used: 0.1, 1 and 10 mg MP. L. After a 24-h period of embryonic exposure, we noted that MP agglomerates were stuck to the D-larvae coat and locomotor eyelashes. We also observed a significant increase in severe malformations and developmental arrests for larvae exposed to MPs ranging from 1 mg MP. L. In terms of swimming behaviour, the maximum speed recorded was lower for larvae exposed at 0.1 and 1 mg MP. L. After an acute exposure to MPs, particles were found in the digestive tract of 3 dpf (days post fertilisation) D-larvae. After 1-h exposure, the concentrations tested (0.1, 1 and 10 mg MP. L) resulted in respectively 38%, 86% and 98%. The larvae swimming behaviour was recorded and analysed. Unlike the results observed at the embryo-larval stage, 3-dpf larvae showed significant impacts with no dose-response effect.
塑料是一种持久的合成聚合物,在海洋环境中作为废物积累。微塑料(MPs,<5 毫米)可以作为身体护理和一些工业产品中的微珠,也可以通过降解作为塑料碎片存在。塑料微珠(1-5 微米,荧光,Cospheric)用于表征 MP 的摄入,并确定它们对牡蛎 D 幼虫(Crassostrea gigas)游泳行为和发育的潜在有害影响。在 24°C 的温度下,胚胎首先暴露于 MPs 中 24 小时。此外,3 日龄的 D 幼虫在相同温度下暴露 1、3 和 5 小时。使用了三种浓度的 MPs:0.1、1 和 10 毫克 MPs。L。经过 24 小时的胚胎暴露期,我们注意到 MPs 聚集体粘在 D 幼虫的外壳和运动睫毛上。我们还观察到,暴露于 1 毫克 MPs 的幼虫严重畸形和发育停滞的比例显著增加。在游泳行为方面,暴露于 0.1 和 1 毫克 MPs 的幼虫的最大速度较低。L.在急性暴露于 MPs 后,在 3 dpf(受精后天数)的 D 幼虫的消化道中发现了颗粒。在 1 小时暴露后,测试的浓度(0.1、1 和 10 毫克 MPs。L)分别导致 38%、86%和 98%。记录并分析了幼虫的游泳行为。与胚胎-幼虫阶段观察到的结果不同,3-dpf 幼虫表现出显著影响,没有剂量反应效应。