刘旻昊, 张振忠, 刘聪, 崔旭梦, 汝少国, 王军. 环境浓度扑草净存在下聚苯乙烯纳米塑料对隐秘小环藻的毒性效应[J]. 海洋环境科学. DOI: 10.12111/j.mes.2023-x-0252
引用本文: 刘旻昊, 张振忠, 刘聪, 崔旭梦, 汝少国, 王军. 环境浓度扑草净存在下聚苯乙烯纳米塑料对隐秘小环藻的毒性效应[J]. 海洋环境科学. DOI: 10.12111/j.mes.2023-x-0252
LIU Minhao, ZHANG Zhenzhong, LIU Cong, CUI Xumeng, RU Shaoguo, WANG Jun. Toxic effects of polystyrene nanoplastics on Cyclotella cryptica in the presence of environmental concentrations of prometryn[J]. Chinese Journal of MARINE ENVIRONMENTAL SCIENCE. DOI: 10.12111/j.mes.2023-x-0252
Citation: LIU Minhao, ZHANG Zhenzhong, LIU Cong, CUI Xumeng, RU Shaoguo, WANG Jun. Toxic effects of polystyrene nanoplastics on Cyclotella cryptica in the presence of environmental concentrations of prometryn[J]. Chinese Journal of MARINE ENVIRONMENTAL SCIENCE. DOI: 10.12111/j.mes.2023-x-0252

环境浓度扑草净存在下聚苯乙烯纳米塑料对隐秘小环藻的毒性效应

Toxic effects of polystyrene nanoplastics on Cyclotella cryptica in the presence of environmental concentrations of prometryn

  • 摘要: 纳米塑料(nanoplastics, NPs)与除草剂扑草净是海洋环境中的常见污染物,但是它们同时存在对海洋微藻的潜在危害尚不清楚。本文探究了环境浓度扑草净(500 ng/L)与聚苯乙烯纳米塑料(70 nm, 20 μg/L、200 μg/L和2000 μg/L)对隐秘小环藻(Cyclotella cryptica)的联合毒性作用。结果表明,20 μg/L、200 μg/L和2000 μg/L NPs能够显著降低隐秘小环藻的光合色素含量、损伤藻细胞结构、抑制隐秘小环藻的种群增长,而500 ng/L扑草净单独暴露并未对隐秘小环藻的早期生长产生显著影响。在500 ng/L扑草净存在下,NPs暴露对隐秘小环藻生长抑制作用会增强,尤其是扑草净与2000 μg/L NPs联合暴露24 h后的藻密度比2000 μg/L NPs单独暴露组降低了19.4%。环境浓度扑草净的存在还会加重NPs对藻细胞的损伤,使膜通透性增大至对照组的1.6倍。细胞膜受损降低了藻细胞对NPs的抵御能力,从而加重了NPs对隐秘小环藻的毒性作用。与2000 μg/L NPs单独暴露组相比,扑草净与2000 μg/L NPs联合暴露下的藻细胞在暴露144 h后的死亡率与异形细胞比例分别升高了4.1%和3.4%。本文研究结果可为评估NPs和除草剂污染对海洋初级生产力的危害提供参考。

     

    Abstract: Nanoplastics (NPs) and herbicide prometryn are common pollutants in the marine environments, but their joint impacts on marine microalgae is unclear. In this study, we investigated the toxic effects of environmental concentrations of prometryn (500 ng/L) and polystyrene nanoplastics (70 nm, 20, 200, and 2000 μg/L) on Cyclotella cryptica. The results showed that 20, 200 and 2000 μg/L NPs significantly reduced photosynthetic pigment content, damaged algal cell structure, and hindered the population growth of C. cryptica. Whereas 500 ng/L prometryn had no significant effect on the early growth of C. cryptica. In the presence of environmental concentrations of prometryn, NPs-induced growth inhibition was significantly enhanced, especially after 24 h of exposure; algal density in the prometryn and 2000 μg/L NPs combined exposure groups was reduced by 19.4% compared with that of the 2000 μg/L NPs single exposure group. Moreover, the environmental concentrations of prometryn aggravated the damage of NPs to the algal cells, which increased the membrane permeability to 1.6 times that of the control group (P < 0.05). Damage to the cell membrane reduced the ability of algal cells to resist the NPs and thus exacerbated the toxicity of NPs to C. cryptica. Compared to the 2000 μg/L NPs single exposure, the combined exposure of prometryn and 2000 μg/L NPs increased the mortality and proportion of anomalous cells by 4.1% and 3.4%, respectively. The results of this study provide a reference for assessing the hazards of NPs and herbicide pollution on marine primary productivity.

     

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