Preparation of Zinc Oxide Nanorods Array and Its Application in Photocatalytic Degradation of Phenol Wastewater

Hui-ling Du, Fenglin Wang, Bao-yuan Pan, P. Dong, M. Qu
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The ZnO nanorod arrays prepared under the action of pulsed electromagnetic field (PEMF) have greater order than that prepared by conversional hydrothermal synthesis. The catalytic performance of ZnO nanorod arrays prepared with PEMF is better accordingly. Introduction Phenol is a kind of extremely nerve poison and causticity chemical substance, which is harmful to all life-form, especially to aquatic life. The characters of phenol wastewater are non-biodegradable, wide source, and seriously hazardous [1-4] . It is necessary for phenol wastewater treatment to find an effective technology. The treatment methods of phenol wastewater include traditional technology and advanced oxidation processes. However, traditional methods such as physical adsorption, coagulation, chemical oxidation and biological treatment are likely to cause secondary pollution [5,6] . Photocatalysis technique as an important advanced oxidation technology is widely researched in organic wastewater treatment. Owing to the small size effect, high surface effect and quantum size effect, nano particles exhibit excellent characters in catalyst fields [7-12] . Nanometer materials such as titanium dioxide and zinc oxide are usually used as photocatalysts to degrade organic pollutants [7,8,10-12] . Previous research has shown that the degradation effects of phenolic wastewater are satisfied using ZnO nanoparticles or ZnO thin as photocatalysts [12-16] . Especially supported nanometer ZnO is characterized by not easy to run off, easy to recover and separate, no secondary pollution in the process of wastewater treatment. In this study, ZnO nanorod arrays are prepared by the hydrothermal synthesis, and the ZnO nanorod samples are used as catalysts to treat simulated wastewater of phenol. Experimental Main chemicals. C6H6O (Tianjin Tianda Chemical Experimental Plant), ZnCl2 (Yanggu Zhongtian Zinc Industry Co., Ltd.), Zn(Ac)2 (Shanghai Xinbao Fine Chemical Plant), C2H5ONH4 (Tianjin Damao Chemical Reagent Factory), C11H13N3O (Tianjin Jinbei Fine Chemical Co., Ltd.) and K3Fe(CN)6 (Tianjin Tianyi Chemical Reagent Factory) were of analytical grade and used as received without further purification. Preparation of ZnO nanorod array. When reaction time was 4 h, Zinc chloride precursor solution concentration was 0.12 mol/L and reaction temperature was 90°C, ZnO nanorod array sample 1 was synthesized via a hydrothermal method [17] . The ZnO nanorod array sample 2 was prepared under similar conditions as those of sample 1, but with the presence of the external electromagnetic field(parameters: pulsed voltage 400 V, pulsed frequency 5 Hz, treatment time 60 s) which was used before the reactor was put into the constant temperature drying oven(see Figure 1). 7 Figure 1. The preparation scheme of ZnO nanorod arrays. Characterization of ZnO nanorod. X-ray diffraction was applied to determining the phase structure, performed on a D/max-Rigaku XRD diffraction spectrometer with 2θ ranging from 20° to 80°, using Cu Kα radiation(λ=0.154178 nm). Morphologies of the samples were studied by scanning electron microscopy (SEM) (HITACHI S-3000 N). Photocatalytic activity tests. The photocatalytic activities of ZnO nanorod samples were evaluated by the degradation of simulated phenol wastewater under UV light irradiation. The distance between ultraviolet lamp and wastewater liquid level was 8 cm. The reaction temperature was 20°C. In each experiment, the sample was put into phenol wastewater (100 mL) containing phenol (5 mg). According to Water quality—Determination of volatile phenolic compounds—4-AAP spectrophotometric method(HJ 503-2009), the volatile phenolic compounds remaining in the solution after the photodegradation process was measured using a 722N visible spectrophotometer. Results and Discussions Characterization of ZnO nanorod arrays. The ZnO nanorod sample 1 and sample 2 were characterized with respect to morphology by SEM. The SEM images of sample 1 and sample 2 are depicted in Figure 2 and Figure 3, respectively. The effects of PEMF on the morphology and size of the ZnO nanorod can be demonstrated with these SEM micrographs. The average diameter, average length and aspect ratios of samples are shown in Table 1. Table 1. 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Abstract

ZnO nanorod arrays were prepared by the hydrothermal synthesis. SEM images were used to observe the morphologies of ZnO nanorod arrays. The phase structures of ZnO nanorod arrays were characterized by means of XRD. The phenol wastewater was degraded with ZnO nanorod as catalyst. The effects of UV light application time and ZnO nanorod catalyst quantity on phenol removal efficiency were investigated. The results show that the phenol removal efficiency is as high as 70.12% when 5.7 mg ZnO nanorod catalyst is added, pH is 7.3, and UV light application time is 2 h. The ZnO nanorod arrays prepared under the action of pulsed electromagnetic field (PEMF) have greater order than that prepared by conversional hydrothermal synthesis. The catalytic performance of ZnO nanorod arrays prepared with PEMF is better accordingly. Introduction Phenol is a kind of extremely nerve poison and causticity chemical substance, which is harmful to all life-form, especially to aquatic life. The characters of phenol wastewater are non-biodegradable, wide source, and seriously hazardous [1-4] . It is necessary for phenol wastewater treatment to find an effective technology. The treatment methods of phenol wastewater include traditional technology and advanced oxidation processes. However, traditional methods such as physical adsorption, coagulation, chemical oxidation and biological treatment are likely to cause secondary pollution [5,6] . Photocatalysis technique as an important advanced oxidation technology is widely researched in organic wastewater treatment. Owing to the small size effect, high surface effect and quantum size effect, nano particles exhibit excellent characters in catalyst fields [7-12] . Nanometer materials such as titanium dioxide and zinc oxide are usually used as photocatalysts to degrade organic pollutants [7,8,10-12] . Previous research has shown that the degradation effects of phenolic wastewater are satisfied using ZnO nanoparticles or ZnO thin as photocatalysts [12-16] . Especially supported nanometer ZnO is characterized by not easy to run off, easy to recover and separate, no secondary pollution in the process of wastewater treatment. In this study, ZnO nanorod arrays are prepared by the hydrothermal synthesis, and the ZnO nanorod samples are used as catalysts to treat simulated wastewater of phenol. Experimental Main chemicals. C6H6O (Tianjin Tianda Chemical Experimental Plant), ZnCl2 (Yanggu Zhongtian Zinc Industry Co., Ltd.), Zn(Ac)2 (Shanghai Xinbao Fine Chemical Plant), C2H5ONH4 (Tianjin Damao Chemical Reagent Factory), C11H13N3O (Tianjin Jinbei Fine Chemical Co., Ltd.) and K3Fe(CN)6 (Tianjin Tianyi Chemical Reagent Factory) were of analytical grade and used as received without further purification. Preparation of ZnO nanorod array. When reaction time was 4 h, Zinc chloride precursor solution concentration was 0.12 mol/L and reaction temperature was 90°C, ZnO nanorod array sample 1 was synthesized via a hydrothermal method [17] . The ZnO nanorod array sample 2 was prepared under similar conditions as those of sample 1, but with the presence of the external electromagnetic field(parameters: pulsed voltage 400 V, pulsed frequency 5 Hz, treatment time 60 s) which was used before the reactor was put into the constant temperature drying oven(see Figure 1). 7 Figure 1. The preparation scheme of ZnO nanorod arrays. Characterization of ZnO nanorod. X-ray diffraction was applied to determining the phase structure, performed on a D/max-Rigaku XRD diffraction spectrometer with 2θ ranging from 20° to 80°, using Cu Kα radiation(λ=0.154178 nm). Morphologies of the samples were studied by scanning electron microscopy (SEM) (HITACHI S-3000 N). Photocatalytic activity tests. The photocatalytic activities of ZnO nanorod samples were evaluated by the degradation of simulated phenol wastewater under UV light irradiation. The distance between ultraviolet lamp and wastewater liquid level was 8 cm. The reaction temperature was 20°C. In each experiment, the sample was put into phenol wastewater (100 mL) containing phenol (5 mg). According to Water quality—Determination of volatile phenolic compounds—4-AAP spectrophotometric method(HJ 503-2009), the volatile phenolic compounds remaining in the solution after the photodegradation process was measured using a 722N visible spectrophotometer. Results and Discussions Characterization of ZnO nanorod arrays. The ZnO nanorod sample 1 and sample 2 were characterized with respect to morphology by SEM. The SEM images of sample 1 and sample 2 are depicted in Figure 2 and Figure 3, respectively. The effects of PEMF on the morphology and size of the ZnO nanorod can be demonstrated with these SEM micrographs. The average diameter, average length and aspect ratios of samples are shown in Table 1. Table 1. The average diameter, average length and aspect ratios of samples. sample average diameter(nm) average length(nm) aspect ratio sample 1 30
氧化锌纳米棒阵列的制备及其在光催化降解苯酚废水中的应用
采用水热合成法制备了ZnO纳米棒阵列。利用扫描电镜观察了ZnO纳米棒阵列的形貌。采用XRD对ZnO纳米棒阵列的相结构进行了表征。以ZnO纳米棒为催化剂对苯酚废水进行了降解。考察了紫外光照射时间和氧化锌纳米棒催化剂用量对苯酚去除率的影响。结果表明,当ZnO纳米棒催化剂添加量为5.7 mg、pH值为7.3、紫外光作用时间为2 h时,苯酚的去除率高达70.12%。脉冲电磁场(PEMF)作用下制备的ZnO纳米棒阵列比转化水热合成法制备的ZnO纳米棒阵列有序度更高。用PEMF制备的ZnO纳米棒阵列的催化性能也相应较好。苯酚是一种极具神经毒性和腐蚀性的化学物质,对所有生物,尤其是水生生物都有害。苯酚废水具有不可生物降解、来源广、危害严重等特点[1-4]。寻找一种有效的工艺是处理含酚废水的必要条件。苯酚废水的处理方法包括传统工艺和高级氧化工艺。而传统的物理吸附、混凝、化学氧化、生物处理等方法容易造成二次污染[5,6]。光催化技术作为一种重要的高级氧化技术在有机废水处理中得到了广泛的研究。由于小尺寸效应、高表面效应和量子尺寸效应,纳米颗粒在催化剂领域表现出优异的性能[7-12]。二氧化钛、氧化锌等纳米材料通常作为光催化剂用于降解有机污染物[7,8,10-12]。已有研究表明,采用纳米氧化锌或薄氧化锌作为光催化剂,可以满足对含酚废水的降解效果[12-16]。特别是负载型纳米ZnO具有不易流失、易于回收分离、在废水处理过程中无二次污染等特点。本研究采用水热合成法制备了ZnO纳米棒阵列,并将ZnO纳米棒样品作为催化剂处理苯酚模拟废水。主要化学品。c6h60(天津天达化学实验厂)、ZnCl2(阳谷中天锌业有限公司)、Zn(Ac)2(上海新宝精细化工厂)、C2H5ONH4(天津达茂化学试剂厂)、c11h13n30(天津金杯精细化工有限公司)和K3Fe(CN)6(天津天一化学试剂厂)为分析级,收来即用,无需进一步提纯。ZnO纳米棒阵列的制备。当反应时间为4 h,氯化锌前驱体溶液浓度为0.12 mol/L,反应温度为90℃时,采用水热法合成ZnO纳米棒阵列样品1[17]。制备的ZnO纳米棒阵列样品2的制备条件与样品1相似,但在将反应器放入恒温干燥箱之前,使用了外部电磁场(参数为脉冲电压400 V,脉冲频率5 Hz,处理时间60 s)(见图1)。ZnO纳米棒阵列的制备方案。ZnO纳米棒的表征。采用Cu Kα辐射(λ=0.154178 nm),在2θ范围为20°~ 80°的D/max-Rigaku XRD衍射仪上进行了相结构的测定。利用扫描电镜(SEM) (HITACHI S-3000 N)研究了样品的形貌。通过紫外光照射对模拟苯酚废水的降解,考察了ZnO纳米棒样品的光催化活性。紫外灯与废水液面距离为8 cm。反应温度为20℃。每次实验将样品放入含苯酚(5 mg)的苯酚废水(100 mL)中。根据《水质挥发性酚类化合物测定- 4- aap分光光度法》(HJ 503-2009),采用722N可见分光光度仪测定光降解过程后溶液中残留的挥发性酚类化合物。ZnO纳米棒阵列表征的结果与讨论。用SEM对ZnO纳米棒样品1和样品2进行了形貌表征。样品1和样品2的SEM图像分别如图2和图3所示。这些SEM显微图可以证明PEMF对ZnO纳米棒形貌和尺寸的影响。样品的平均直径、平均长度和纵横比见表1。表1。样品的平均直径、平均长度和纵横比。样品平均直径(nm)平均长度(nm)宽高比样品1 30
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