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首页> 外文期刊>Scientific reports. >TiO2 decorated functionalized halloysite nanotubes (TiO2@HNTs) and photocatalytic PVC membranes synthesis, characterization and its application in water treatment
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TiO2 decorated functionalized halloysite nanotubes (TiO2@HNTs) and photocatalytic PVC membranes synthesis, characterization and its application in water treatment

机译:TiO2装饰官能化霍利石纳米管(TiO2 @ HNT)和光催化PVC膜的合成,表征及其在水处理中的应用

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In this study photocatalyst, TiO2@HNTs were prepared by synthesizing TiO2 nanoparticles in situon the functionalized halloysite nanotubes (HNTs) surface. Photocatalytic PVC membrane TiO2@HNTs M2 (2wt.%) and TiO2@HNTs M3 (3wt.%) were also prepared. Photocatalyst TiO2@HNTsand photocatalytic PVC membranes were used to study the photocatalytic activity against themethylene blue (MB) and rhodamine B (RB) dyes in UV batch reactor. The structure and morphologyof photocatalyst and photocatalytic PVC membrane were characterized by fourier transforminfrared spectroscopy (FT-IR), X-ray difraction (XRD), scanning electron microscopy (SEM), energydispersive X-ray (EDX), transmission electron microscopy (TEM), UV-Vis spectrophotometer andphotoluminescence (PL). The PL study showed that the oxygen vacancies and surface hydroxyl groupspresent on the surface of TiO2@HNTs act as excellent traps for charge carrier, reducing the electronholerecombination rate.TiO2@HNTs 2 (2wt.%) and TiO2@HNTs 3 (3wt.%) degraded MB dye up to83.21%, 87.47% and RB dye up to 96.84% and 96.87%, respectively. TiO2@HNT photocatalyst provedto be stable during the three consecutive cycle of photocatalytic degradation of the RB dye. TiO2@HNTs M2 and TiO2@HNTs M3 degraded MB dye up to 27.19%, 42.37% and RB dye up to 30.78%,32.76%, respectively. Photocatalytic degradation of both the dyes followed the frst-order kineticmodel. Degradation product analysis was done using the liquid chromatography–mass spectrometry(LC-MS) and the results showed that the dye degradation was initiated by demethylation of themolecule. MB and RB dye degradation reaction were tested by TBA and IPA as OH* and H+ scavengersrespectively. Mechanism of photocatalytic activity of TiO2@HNTs and photocatalytic PVC membranewere also explained.
机译:在该研究中,通过在官能化的霍氏石英纳米管(HNT)表面中合成TiO 2纳米颗粒来制备TiO 2 @ HNT。还制备了光催化PVC膜TiO2 @ HNTs M2(2wt。%)和TiO2 @ HNT M3(3wt。%)。光催化剂TiO2 @ HNTsand光催化PVC膜用于研究UV批量反应器中对亚乙二(MB)和罗丹明B(RB)染料的光催化活性。光催化剂和光催化PVC膜的结构和形态学通过傅里叶变换荧光磷酸纤维素(FT-IR),X射线差异(XRD),扫描电子显微镜(SEM),透射电子显微镜(TEM),扫描电子显微镜(SEM),透射电子显微镜(TEM) ,UV-Vis分光光度计和PLOPOLMINECENCE(PL)。 PL研究表明,TiO 2的表面上的氧空位和表面羟基的羟基缩须作为电荷载体的优异陷阱,减少了电气聚集率。氧化物结合率为2(2wt.%)和TiO 2 @ HNT 3(3wt。% )将MB染料降解,高达83.21%,87.47%和RB染料,分别高达96.84%和96.87%。 TiO2 @HNT光催化在RB染料的光催化降解的三个连续循环期间证明是稳定的。 TiO2 @ HNTs M2和TiO2 @ HNT M3降解了MB染料,可分别高达27.19%,42.37%和RB染料,分别为30.78%,32.76%。染料的光催化降解染料术后染料序列。使用液相色谱 - 质谱法(LC-MS)进行降解产物分析,结果表明,通过分子的去甲基化引发染料劣化。通过TBA和IPA测试MB和RB染料降解反应为OH *和H +清除术。 TiO2 @ HNT和光催化PVC膜的光催化活性的机理也解释说明。

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