老化聚苯乙烯微球在日本虎斑猛水蚤体内的摄入排出动力学及氧化应激效应

Study on the uptake and depuration kinetics and oxidative stress effect of colonized polystyrene microspheres in Tigriopus japonicus

  • 摘要: 微塑料具有尺寸小、难降解以及易于被生物体吸收利用等特点,对海洋生态系统构成潜在威胁。海洋生物摄入微塑料后可在消化道等不同组织和器官中蓄积或转移,进而引起一系列生物学效应。然而,当前的海洋生态毒理学研究缺乏老化作用等真实环境因素考量。本研究以海洋桡足类日本虎斑猛水蚤(Tigriopus japonicus)为受试生物,考察了天然海水老化作用下猛水蚤对10 μm聚苯乙烯(polystyrene, PS)微球(暴露浓度为100个/mL、1000个/mL)的摄入排出动力学及抗氧化防御机制。研究发现,老化作用导致猛水蚤对PS微球的摄入量增加,且摄入量随暴露时间增加(3 h、6 h、12 h、24 h和48 h)呈现先增加后降低的趋势,48 h后猛水蚤对暴露浓度为1000个/mL的老化PS微球的摄入量(4.6 ± 0.5)个/只是未老化PS微球(2.5 ± 0.1)个/只的1.9倍。老化作用对猛水蚤体内PS微球的排出过程几乎没有影响,48 h后猛水蚤体内老化和未老化PS微球残留百分比仍相对较高(> 30%)。低浓度(100个/mL)暴露条件下,与未老化PS微球相比,老化PS微球显著诱导猛水蚤体内超氧化物歧化酶(SOD)和谷胱甘肽S转移酶(GST)活性,上调相关基因(MnSOD、GST、GRGPx)表达,抑制过氧化氢酶(CAT)活性并下调CAT基因相对表达量;另外,PS微球暴露浓度越高对猛水蚤抗氧化防御系统的损伤程度越高。总体而言,老化作用提高了猛水蚤对PS微球的摄入能力,在一定程度上加剧了氧化应激效应。研究结果可为科学评估真实海洋环境中的微塑料生态风险提供科学依据。

     

    Abstract: Microplastics pose a potential threat to marine ecosystems due to their small size and not readily degradable. Microplastics ingested by marine organisms can accumulate or transfer in different tissues and organs, such as the digestive tract, and cause a series of biological effects. However, current toxicological studies lack the consideration of natural environmental factors, such as the role of aging. In this study, the marine copepod Tigriopus japonicus was used as the test organism; we investigated the toxicokinetic process and antioxidant defense mechanism of T. japonicus under natural seawater colonization in response to 10 μm polystyrene (PS) microspheres (exposed at concentrations of 100 particles/mL and 1000 particles/mL). It was found that the colonized effect increased the uptake of PS microspheres by T. japonicus, and the uptake tended to increase and then decrease with the exposure time (3 h, 6 h, 12 h, 24 h, and 48 h). After 48 h of exposure, T. japonicus ingested 1.9 times more highly concentrated (1000 particles/mL) colonized PS microspheres (4.6 ± 0.5)/individual than pristine PS microspheres (2.5 ± 0.1)/individual. Colonization had almost no effect on the excretion process of PS microspheres in T. japonicus. The residual percentage of PS microspheres in T. japonicus remained relatively high (> 30%) after 48 h. Under the low concentration (100 particles/mL) exposure condition, colonized PS microspheres significantly induced superoxide dismutase (SOD) and glutathione S-transferase (GST) activities, up-regulated the expression of related genes (MnSOD, GST, GR, and GPx), inhibited catalase (CAT) activity and down-regulated the relative expression of CAT genes in T. japonicus compared with that of pristine PS microspheres, and higher concentrations of PS microspheres caused greater damage to the antioxidant defense system of T. japonicus. Overall, the colonization effect increased the uptake of PS microspheres by T. japonicus, which exacerbated the oxidative stress in T. japonicus caused by the colonized PS microspheres to a certain extent. The results of the study are informative for scientific assessment of the ecological risk of microplastics in real marine environments. Our findings contributed to the scientific ecological risk assessment of microplastics in the natural marine environment.

     

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