Spanish Institute of Oceanography, IEO, Oceanographic Center of Murcia, Varadero 1, E-30740 San Pedro del Pinatar, Murcia, Spain.
Spanish Institute of Oceanography, IEO, Oceanographic Center of Murcia, Varadero 1, E-30740 San Pedro del Pinatar, Murcia, Spain.
Ecotoxicol Environ Saf. 2019 May 30;173:103-109. doi: 10.1016/j.ecoenv.2019.02.020. Epub 2019 Feb 12.
It is highly likely that phytoplanktonic organisms will interact with MPs in the ocean, and consequently with the pollutants sorbed onto their surfaces. Microalgae play an essential role in maintaining the balance of the marine ecosystem due to the fact that they are a primary producer and the base of marine trophic chains. Therefore, their fitness represents an important index in the assessment of water quality. The objectives of this study were i) to assess the toxicity of MPs and the pesticide chlorpyrifos (CPF) to the microalgae, Isochrysis galbana, clone t-ISO and ii) to ascertain whether the presence of MPs affects the toxicity of CPF. Microalgae growth rate was selected as the endpoint and a commercial virgin PE micronized powder was chosen as a micro-plastic model, with mean size ranging from 2 to 6 µm, assayed until 25 mg L. CPF was tested at concentrations ranging from 0 to 4 mg L. A constant concentration of MPs (5 mg L) was loaded with increasing doses of CPF (0-3 mg L) with a 2 h incubation period. Bioassays were performed at 20 °C, in glass tubes of 50 ml, with air and constant light and an exposure time of 72 h. Cell counts were performed using a Coulter Counter Multisizer III and HPLC was used to quantify the partition of this pollutant among MPs and water. Although microalgae growth was not impacted by MPs, growth was clearly affected by exposure to CPF from 2 mg L and above, with a total growth inhibition at concentrations over 3 mg L. Subsequent to incubation, 80% of CPF was sorbed onto MP surfaces. Two different dose-response curves resulted from CPF bioassays depending on the presence of MP, with lower percentages of inhibition when CPF was presented through MP. Thus, the adsorption of CPF onto MP surfaces modulates the toxicity of CPF on I. galbana growth through a reduction in its toxicity, as CPF is adsorbed onto MP surfaces which are less bio-available to the algal cells.
浮游植物极有可能与海洋中的 MPs 相互作用,从而与吸附在其表面的污染物相互作用。微藻在维持海洋生态系统平衡方面发挥着重要作用,因为它们是初级生产者,也是海洋食物链的基础。因此,它们的适应性是评估水质的一个重要指标。本研究的目的是:i)评估 MPs 和农药毒死蜱 (CPF) 对微藻,即小球藻克隆 t-ISO 的毒性;ii)确定 MPs 的存在是否会影响 CPF 的毒性。微藻生长速度被选为终点,选择商业 virgin PE 微米化粉末作为微塑料模型,平均粒径为 2 至 6 µm,测试至 25 mg/L。CPF 的测试浓度范围为 0 至 4 mg/L。将一个恒定浓度的 MPs(5 mg/L)与不断增加剂量的 CPF(0-3 mg/L)混合,孵育期为 2 小时。生物测定在 20°C 下进行,在 50 ml 的玻璃管中,用空气和恒定光照,暴露时间为 72 小时。细胞计数使用库尔特计数器 Multisizer III 进行,HPLC 用于定量这种污染物在 MPs 和水中的分配。虽然微藻的生长不受 MPs 的影响,但暴露于 2 mg/L 及以上的 CPF 时,生长明显受到影响,浓度超过 3 mg/L 时,生长完全受到抑制。孵育后,80%的 CPF 被吸附到 MPs 表面。由于 CPF 是通过 MPs 呈现的,因此 CPF 生物测定产生了两条不同的剂量-反应曲线,当 CPF 呈现在 MPs 上时,抑制百分比较低。因此,CPF 吸附到 MPs 表面通过降低其毒性来调节 CPF 对小球藻生长的毒性,因为 CPF 被吸附到 MPs 表面,这些表面对藻类细胞的生物利用度较低。