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可见光辐照下掺铝氧化锌纳米粒子增强的光催化去除蓝藻毒素。

Enhanced Photocatalytic Removal of Cyanotoxins by Al-Doped ZnO Nanoparticles with Visible-LED Irradiation.

机构信息

Laboratory of Physics of Materials and Nanomaterials Applied at Environment (LaPhyMNE), Faculty of Sciences, University of Gabes, Erriadh Manara Zrig, 6072 Gabes, Tunisia.

Thin Films and Nanostructures Electrodeposition Group (GE-CPN), Department of Materials Science and Physical Chemistry, University of Barcelona, Martí i Franquès 1, E-08028 Barcelona, Spain.

出版信息

Toxins (Basel). 2021 Jan 17;13(1):66. doi: 10.3390/toxins13010066.

DOI:10.3390/toxins13010066
PMID:33477326
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7829790/
Abstract

The ZnO-based visible-LED photocatalytic degradation and mineralization of two typical cyanotoxins, microcystin-LR (MC-LR), and anatoxin-A were examined. Al-doped ZnO nanoparticle photocatalysts, in Al:Zn ratios between 0 and 5 at.%, were prepared via sol-gel method and exhaustively characterized by X-ray diffraction, transmission electron microscopy, UV-vis diffuse reflectance spectroscopy, photoluminescence spectroscopy, and nitrogen adsorption-desorption isotherms. With both cyanotoxins, increasing the Al content enhances the degradation kinetics, hence the use of nanoparticles with 5 at.% Al content (A5ZO). The dosage affected both cyanotoxins similarly, and the photocatalytic degradation kinetics improved with photocatalyst concentrations between 0.5 and 1.0 g L. Nevertheless, the pH study revealed that the chemical state of a species decisively facilitates the mutual interaction of cyanotoxin and photocatalysts. A5ZO nanoparticles achieved better outcomes than other photocatalysts to date, and after 180 min, the mineralization of anatoxin-A was virtually complete in weak alkaline medium, whereas only 45% of MC-LR was in neutral conditions. Moreover, photocatalyst reusability is clear for anatoxin-A, but it is adversely affected for MC-LR.

摘要

研究了基于 ZnO 的可见光-LED 光催化降解和两种典型的蓝藻毒素(微囊藻毒素-LR(MC-LR)和鱼腥藻毒素-A)的矿化。通过溶胶-凝胶法制备了 Al 掺杂 ZnO 纳米粒子光催化剂,Al:Zn 比为 0 至 5 at.%,并通过 X 射线衍射、透射电子显微镜、紫外-可见漫反射光谱、光致发光光谱和氮吸附-脱附等温线进行了详尽的表征。对于这两种蓝藻毒素,增加 Al 含量都会增强降解动力学,因此使用 Al 含量为 5 at.%的纳米颗粒(A5ZO)。两种蓝藻毒素的剂量影响相似,光催化剂浓度在 0.5 和 1.0 g/L 之间时,光催化降解动力学得到改善。然而,pH 值研究表明,物种的化学状态会显著促进蓝藻毒素与光催化剂的相互作用。A5ZO 纳米粒子比迄今为止的其他光催化剂取得了更好的效果,在 180 分钟后,在弱碱性介质中鱼腥藻毒素-A 的矿化几乎完全,而在中性条件下只有 45%的微囊藻毒素-LR 被矿化。此外,光催化剂对鱼腥藻毒素-A 的可重复使用性很明显,但对微囊藻毒素-LR 的可重复使用性则受到不利影响。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/d7a2761badb2/toxins-13-00066-sch001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/9ae2d319e35f/toxins-13-00066-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/6f42ab740bb9/toxins-13-00066-g002.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/788cfdd2572c/toxins-13-00066-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/cbf998059f51/toxins-13-00066-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/d7a2761badb2/toxins-13-00066-sch001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/9ae2d319e35f/toxins-13-00066-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/6f42ab740bb9/toxins-13-00066-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/48a492f1eb15/toxins-13-00066-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/0c0f1e3d496a/toxins-13-00066-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/788cfdd2572c/toxins-13-00066-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/cbf998059f51/toxins-13-00066-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/4682/7829790/d7a2761badb2/toxins-13-00066-sch001.jpg

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