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Optimization of ZnO-NPs to Investigate Their Safe Application by Assessing Their Effect on Soil Nematode Caenorhabditis elegans

机译:通过评估ZnO-NP对土壤线虫秀丽隐杆线虫的作用来研究其安全应用的优化

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摘要

Zinc oxide nanoparticles (ZnO-NPs) are increasingly receiving attention due to their widespread application in cosmetics, pigments and coatings. This has raised concerns in the public and scientific communities regarding their unexpected health effects. Toxicity effect of ZnO-NPs on the environment was assessed in the present study using Caenorhabditis elegans. Multiple toxicity end points including their mortality, behaviour, reproduction, in vitro distribution and expression of stress response mtl-1 and sod-1 genes were observed to evaluate safe application of ZnO-NPs. C. elegans were exposed to 10, 50, and 100 nm ZnO-NPs (0.1 to 2.0 g/l). Application of 10 nm ≥0.7g/l adversely affects the survivability of worms and was significantly not affected with exposure of 50 and 100 nm ≤1.0 g/l. However, reproduction was affected at much low concentration as compared to their survivability. LC50 was recorded 1.0 ± 0.06 (g/l) for 100 nm, 0.90 ± 0.60 for 50 nm and 0.620 ± 0.08 for 10 nm. Expression of mtl-1 and sod-1 was significantly increased with application of 10 nm ≥0.7g/l and significantly unaffected with exposure of 50 and 100 nm at the same concentration. ZnO-NPs (10 nm) had shown even distribution extended nearly the entire length of the body. The distribution pattern of ZnO-NPs indicates that the intestine is the major target tissues for NP toxicity. Study demonstrates that small-sized (10 nm) ZnO-NPs ≥0.7g/l is more toxic than larger-sized particles. This may be suggested on the basis of available data; application of 50 and 100 nm ≤1.0 g/l ZnO-NPs may be used to the environment as this shows no significant toxicity. However, further calibration is warranted to explore safe dose on soil compartments prior to their field application.
机译:氧化锌纳米颗粒(ZnO-NPs)由于在化妆品,颜料和涂料中的广泛应用而受到越来越多的关注。这已引起公众和科学界对其意外健康影响的关注。在本研究中,使用秀丽隐杆线虫评估了ZnO-NPs对环境的毒性作用。观察到多个毒性终点,包括它们的死亡率,行为,繁殖,体外分布以及应激反应mtl-1和sod-1基因的表达,以评估ZnO-NP的安全应用。秀丽隐杆线虫暴露于10、50和100 nm的ZnO-NPs(0.1至2.0 g / l)。施加10 nm≥0.7g / l会对蠕虫的生存能力产生不利影响,并且在暴露于50和100 nm≤1.0 g / l的情况下不会明显影响蠕虫。但是,与它们的生存能力相比,繁殖受到的影响要低得多。 LC50记录为100 nm 1.0±0.06(g / l),50 nm 0.90±0.60和10 nm 0.620±0.08。当施用10 nm≥0.7g / l时,mtl-1和sod-1的表达显着增加,而在相同浓度下暴露于50和100 nm时,mtl-1和sod-1的表达却未受到明显影响。 ZnO-NP(10 nm)显示出分布均匀,几乎延伸到整个人体长度。 ZnO-NPs的分布模式表明,肠是NP毒性的主要目标组织。研究表明,≥0.7g/ l的小尺寸(10 nm)ZnO-NPs比大尺寸的颗粒更具毒性。可以根据现有数据提出建议; 50和100 nm≤1.0g / l的ZnO-NPs可以用于环境,因为它没有明显的毒性。但是,在进行田间施用之前,有必要进行进一步的校准以探索土壤隔室的安全剂量。

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