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首页> 外文期刊>Reviews of environmental contamination and toxicology >Interaction of Copper-Based Nanoparticles to Soil, Terrestrial, and Aquatic Systems: Critical Review of the State of the Science and Future Perspectives
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Interaction of Copper-Based Nanoparticles to Soil, Terrestrial, and Aquatic Systems: Critical Review of the State of the Science and Future Perspectives

机译：铜基纳米粒子对土壤，陆地和水生系统的相互作用：对科学状态的关键综述与未来的观点

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摘要

In recent years, potential effects of engineered nanoparticles (ENPs), and more so of metallic and metal oxide NPs, on aquatic and terrestrial systems have received increased attention due to their wide applications and consequential release into the environment. Metallic NPs possess unique properties for potential use in the rapidly growing nanotechnology industry (Ali et al. 2015; Arruda et al. 2015; Saleem et al. 2017). Various products containing NPs are currently in the marketplace, and many are still being added to the list (Ahmed et al. 2018b; Rajput et al. 2018c; Vance et al. 2015). The Global Market for Metal Oxide Nanoparticles indicates that the metal oxide NP production could increase from 0.27 million tons (2012) to 1.663 million tons by 2020 (The Global Market for Metal Oxide Nanoparticles to 2020). Among them, Cu-based NPs have wide applications in the field of metallurgy, electronics, automotive, fuel, transportation, machinery, etc. The annual production of Cu was approximately 18.7 million metric tons in 2015 (Keller et al. 2017), out of which a small fraction of approximately 200 tons was comprised of Cu-based NPs (Keller and Lazareva 2013). Since then, the use of Cu-based NPs has been rapidly escalating into applications such as solar cells, sensor development, catalysts, hydrogen production, drug delivery, catalysts for typical C-N cross-coupling reactions, and light-emitting diodes (Keller et al. 2017; Rajput et al. 2017b). Due to their antimicrobial and antifungal properties, Cu-based NPs are suitable for biomedical applications and are also used in water treatment (Ben-Sasson et al. 2016), textile industries (Sedighi and Montazer 2016), food preservation, and agricultural practices (Montes et al. 2016; Ponmurugan et al. 2016; Ray et al. 2015). The rapid production and multifarious applications of Cu-based NPs in various industries have necessitated the assessment of their impacts on the environment (Ahmed et al. 2018b, c).
机译：近年来，在水上和陆地系统上，工程纳米颗粒（ENP）和更多所以金属和金属氧化物NPS的潜在影响由于其广泛的应用和环境释放进入环境，因此受到了增加的关注。金属NPS具有独特的特性，可用于潜在的纳米技术行业（Ali等，2015; Arruda等，2015; Saleem等，2017）。当前包含NPS的各种产品目前在市场上，许多仍在添加到列表中（Ahmed等，2018B; Rajput等，2018C; Vance等，2015）。金属氧化物纳米粒子的全球市场表明，金属氧化物NP产量可能从2020年（2012年）增加到2020吨（2012年）到2020年（金属氧化物纳米颗粒到2020的全球市场）增加到1.663亿吨）。其中，基于Cu的NPS在冶金，电子，汽车，燃料，运输，机械等领域具有广泛的应用。2015年CU的年产量约为1870万公吨（Keller等，2017），Out其中大部分大约200吨由Cu的NPS（Keller和Lazareva 2013）组成。从那时起，基于Cu的NPS已经迅速升级到太阳能电池，传感器开发，催化剂，氢气产量，药物递送，典型CN交叉偶联反应和发光二极管（Keller等。2017; Rajput等人2017B）。由于它们的抗微生物和抗真菌性能，基于Cu的NPS适用于生物医学应用，也用于水处理（Ben-Sasson等，2016），纺织工业（Sedighi和Montazer 2016），食品保存和农业实践（ Montes等。2016; Ponmurugan等。2016; Ray等人。2015）。基于Cu的NP在各个行业的快速生产和多种应用需要评估它们对环境的影响（Ahmed等，2018b，c）。

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