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The developmental toxicity bioaccumulation and distribution of oxidized single walled carbon nanotubes in Artemia salina

机译:盐卤中氧化单壁碳纳米管的发育毒性生物富集和分布

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摘要

With the increasing production and applications of single walled carbon nanotubes (SWCNTs), concerns about the likelihood of SWCNTs being present in the aquatic environment and the subsequent effects on aquatic organisms are emerging. This work aimed to investigate the developmental toxicity, bioaccumulation and distribution of oxidized SWCNTs (O-SWCNTs) in a marine model organism, Artemia salina (A. salina). The results indicated that the hatching rates of capsulated and decapsulated cysts were decreased as the O-SWCNT concentration increased from 0 to 600 mg L–1 at 12, 18, 24 and 36 h. For instar I, II and III larvae exposure to 600 mg L–1, the mean mortality rates were 36.1%, 57.9% and 45.2%, respectively. Both the body length and swimming speed showed a concentration-dependent decrease after exposure to O-SWCNTs for 24 h. The inhibition of swimming may be caused by (1) the malformation of gills; (2) the attachment of O-SWCNTs on the gills. Reactive oxygen species (ROS) and antioxidant enzyme (catalase, superoxide dismutase and glutathione peroxidase) activities substantially increased following exposure, indicating that the toxic effects were related to oxidative stress. O-SWCNTs can be ingested, accumulated and excreted by A. salina, and distributed in the intestine, lipid vesicles and phagocytes. However, the accumulated O-SWCNTs were not completely excreted by A. salina. Uptake kinetics data showed that the O-SWCNT content increased from 1 to 48 h followed by a decrease from 48 to 72 h in the range from 0.08 to 5.7 mg g–1. The combined results so far indicate that O-SWCNTs have the potential to affect aquatic organisms when released into the marine ecosystems.
机译:随着单壁碳纳米管(SWCNT)的生产和应用的增加,人们越来越关注SWCNT在水生环境中的可能性以及对水生生物的后续影响。这项工作旨在调查海洋模型生物卤虫(盐沼)的发育毒性,生物积累和氧化SWCNT(O-SWCNT)的分布。结果表明,随着O-SWCNT浓度在12、18、24和36 h从0毫克L –1 升高,囊化和解囊化囊肿的孵化率降低。 I,II和III龄幼虫在600 mg L –1 中的平均死亡率分别为36.1%,57.9%和45.2%。暴露于O-SWCNT 24小时后,体长和游泳速度均显示出浓度依赖性的下降。游泳的抑制可能是由于(1)ill畸形; (2)O-SWCNT在s上的附着。暴露后,活性氧(ROS)和抗氧化酶(过氧化氢酶,超氧化物歧化酶和谷胱甘肽过氧化物酶)的活性显着增加,表明毒性作用与氧化应激有关。 O-SWCNT可以被食盐曲霉摄入,积累和排泄,并分布在肠,脂质囊泡和吞噬细胞中。然而,积累的O-SWCNTs并没有被盐假单胞菌完全排泄。吸收动力学数据表明,O-SWCNT含量从1到48小时增加,然后从48到72小时减少,范围从0.08到5.7 mg g –1 。迄今为止的综合结果表明,O-SWCNT在释放到海洋生态系统中时有可能影响水生生物。

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