CN110102322B - Preparation method of flower-like Ag@AgBr/ZnO photocatalytic materials - Google Patents
Preparation method of flower-like Ag@AgBr/ZnO photocatalytic materials Download PDFInfo
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- CN110102322B CN110102322B CN201910519670.7A CN201910519670A CN110102322B CN 110102322 B CN110102322 B CN 110102322B CN 201910519670 A CN201910519670 A CN 201910519670A CN 110102322 B CN110102322 B CN 110102322B
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- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
- B01J35/39—Photocatalytic properties
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Abstract
本发明公开了一种花状Ag@AgBr/ZnO光催化材料的制备方法,属于纳米材料制备领域。该方法采用如下步骤:1)配置一定浓度的表面活性剂和Zn源,作为Zn源溶液;配置一定浓度的六亚甲基四胺和Ag源,作为Ag源溶液;2)向Ag源溶液中加入氧化剂,并以一定速率逐滴加入到Zn源溶液中;3)将混合溶液转移至高压反应釜,以一定温度在一定时间下进行水热反应;4)将生成物经水洗醇洗烘干后,在空气中煅烧,冷却至室温后得到花状的Ag@AgBr/ZnO光催化材料。本发明采用的合成方法流程简单,操作简便,无二次污染。合成的光催化材料具有形貌均一、性能优异等特点。本发明工作属于光催化材料领域。
The invention discloses a preparation method of a flower-shaped Ag@AgBr/ZnO photocatalytic material, and belongs to the field of nanometer material preparation. The method adopts the following steps: 1) configuring a certain concentration of surfactant and a Zn source as a Zn source solution; configuring a certain concentration of hexamethylenetetramine and an Ag source as an Ag source solution; 2) adding a solution to the Ag source solution Add oxidizing agent, and add it dropwise to the Zn source solution at a certain rate; 3) transfer the mixed solution to an autoclave, and carry out a hydrothermal reaction at a certain temperature for a certain period of time; 4) Wash the product with water and alcohol and dry it After calcination in air, the flower-like Ag@AgBr/ZnO photocatalytic material was obtained after cooling to room temperature. The synthetic method adopted in the present invention has the advantages of simple process flow, simple and convenient operation, and no secondary pollution. The synthesized photocatalytic materials have the characteristics of uniform morphology and excellent performance. The work of the present invention belongs to the field of photocatalytic materials.
Description
技术领域technical field
本发明涉及花状的Ag@AgBr/ZnO光催化材料的制备方法。The invention relates to a preparation method of flower-shaped Ag@AgBr/ZnO photocatalytic materials.
背景技术Background technique
ZnO是一种广泛应用于光催化氧化技术的半导体催化剂,它拥有着优异的光催化活性、稳定的化学性质和较高的量子产率,因此ZnO在污水处理等方向有着较高的应用价值。然而ZnO是一种宽禁带半导体材料,仅能由紫外光激发光催化氧化反应,对太阳光的利用率仅有4%,且ZnO作为光催化材料,还存在着电子-空穴对复合速率快的问题。这些缺陷限制了其实际应用。为了解决ZnO的这些缺陷,人们进行了一系列的尝试。研究发现,Ag@AgBr等离子体催化剂,由于体系中AgBr分解产生的Ag纳米粒子的等离子体共振效应,Ag@AgBr可以响应可见光进行光催化氧化过程,但是由于其较小的固有带隙,直接用于光催化氧化,效果并不理想。鉴于单一催化剂有着各自的优点和不足,我们将Ag@AgBr和ZnO进行复合,形成复合型催化剂Ag@AgBr/ZnO,大幅度提高了光催化剂对光的利用率,并能够在组分之间产生电子转移,延缓电子-空穴对的复合,提高光催化降解有机物的速度和效率。在环境形势十分严峻的今天,研发高效的复合型光催化剂是迫在眉睫的,既有理论意义,又有实际价值。ZnO is a semiconductor catalyst widely used in photocatalytic oxidation technology. It has excellent photocatalytic activity, stable chemical properties and high quantum yield. Therefore, ZnO has high application value in sewage treatment and other directions. However, ZnO is a wide bandgap semiconductor material, which can only stimulate photocatalytic oxidation reaction by ultraviolet light, and the utilization rate of sunlight is only 4%, and as a photocatalytic material, ZnO also has an electron-hole pair recombination rate. quick question. These defects limit its practical application. In order to solve these defects of ZnO, a series of attempts have been made. The study found that the Ag@AgBr plasmonic catalyst, due to the plasmon resonance effect of Ag nanoparticles generated by the decomposition of AgBr in the system, can respond to visible light for the photocatalytic oxidation process of Ag@AgBr, but due to its small inherent band gap, it can be directly used For photocatalytic oxidation, the effect is not ideal. In view of the advantages and disadvantages of a single catalyst, we composite Ag@AgBr and ZnO to form a composite catalyst Ag@AgBr/ZnO, which greatly improves the utilization rate of light by the photocatalyst and can generate light between the components. Electron transfer, delaying the recombination of electron-hole pairs, and improving the speed and efficiency of photocatalytic degradation of organic matter. In today's severe environmental situation, the development of efficient composite photocatalysts is imminent, which has both theoretical and practical value.
2013年Lei Shi等人在文章《Highly efficient visible light-drivenAg/AgBr/ZnO composite photocatalyst for degrading Rhodamine B》中采用沉积-沉淀法两步法得到AgBr/ZnO光催化材料,再通过光还原法制备棒状Ag/AgBr/ZnO纳米复合材料。在模拟太阳光照射1h的情况下,0.05g此样品对10mg/L的罗丹明B的降解率为94.7%。沉积-沉淀两步法结合光还原法这一制备方法,存在操作复杂、流程繁琐、制备周期长等问题。In 2013, Lei Shi et al. in the article "Highly efficient visible light-drivenAg/AgBr/ZnO composite photocatalyst for degrading Rhodamine B" used a two-step deposition-precipitation method to obtain AgBr/ZnO photocatalytic materials, and then prepared rod-shaped materials by photoreduction method. Ag/AgBr/ZnO nanocomposites. Under the condition of simulated sunlight irradiation for 1h, the degradation rate of 0.05g of this sample to 10mg/L Rhodamine B was 94.7%. The preparation method of the deposition-precipitation two-step method combined with the photoreduction method has problems such as complicated operation, cumbersome process and long preparation period.
2014年Qi Zhang等人在文章《In situ oxidation ofAg/ZnO by bromine waterto prepare ternary Ag-AgBr/ZnO sunlight-derived photocatalyst》中用溴水原位氧化一锅法制备的Ag/ZnO微球,得到球形Ag-AgBr/ZnO复合光催化材料。在300W碘钨灯照射3h的情况下,0.1g此样品对5mg/L的罗丹明B的降解率接近100%。这一制备方法,除制备过程繁琐,制备周期长之外,还存在着球形的Ag-AgBr/ZnO降解效率较低的问题。In 2014, Qi Zhang et al. in the article "In situ oxidation of Ag/ZnO by bromine water to prepare ternary Ag-AgBr/ZnO sunlight-derived photocatalyst" used bromine water in situ oxidation of Ag/ZnO microspheres prepared by one-pot method to obtain spherical Ag-AgBr/ZnO composite photocatalytic material. Under the condition of 300W iodine-tungsten lamp irradiation for 3h, the degradation rate of 0.1g of this sample to 5mg/L Rhodamine B is close to 100%. In addition to the complicated preparation process and long preparation period, this preparation method also has the problem of low degradation efficiency of spherical Ag-AgBr/ZnO.
2011年徐远国等人在会议《Ag/AgBr@ZnO光催化剂的制备及其降解甲基橙的研究》中采用水热法制备Ag/AgBr@ZnO光催化剂。光照3h对甲基橙的降解率约为95%。不难看出,长达3h的降解时间,不能够体现光催化氧化法高效快速的优势。In 2011, Xu Yuanguo et al. used the hydrothermal method to prepare Ag/AgBr@ZnO photocatalyst in the conference "Preparation of Ag/AgBr@ZnO Photocatalyst and Research on Degradation of Methyl Orange". The degradation rate of methyl orange was about 95% under illumination for 3h. It is not difficult to see that the degradation time as long as 3h cannot reflect the high efficiency and rapidity of the photocatalytic oxidation method.
2018年程志鹏等人在专利《多孔Ag/AgBr纳米材料的制备方法》(CN108975383A)中采用水热法制备得到多孔的Ag/AgBr材料。在方法中首先制备出Ag/AgCl/AgBr前驱体,经氨水溶液洗涤去除AgCl后得到Ag/AgBr,制备过程并不是直接指向最终制备的纳米材料,对原料有一定的浪费。In 2018, Cheng Zhipeng et al. used the hydrothermal method to prepare porous Ag/AgBr materials in the patent "Preparation Method of Porous Ag/AgBr Nanomaterials" (CN108975383A). In the method, the Ag/AgCl/AgBr precursor is first prepared, and Ag/AgBr is obtained after the AgCl is removed by washing with ammonia solution. The preparation process is not directly directed to the final prepared nanomaterials, and there is a certain waste of raw materials.
2016年陈设云等人在专利《一种光催化剂Ag/AgBr的制备及其应用》(CN106111166A)中以咪唑基离子液体1-丁基-3-甲基咪唑溴盐([BMIM]Br)作为溴源和前驱体水热制备得到Ag/AgBr光催化剂。值得指出,离子液体会强烈的吸收空气中的水分(即使是疏水性的离子液体),大大降低其性能;而且实际实验中,离子液体价格高,纯度低(受制备过程限制),一旦混有杂质,也会影响其性能,限制了其实际的应用能力。In 2016, Chen Shenyun et al. used imidazolium-based ionic liquid 1-butyl-3-methylimidazolium bromide ([BMIM]Br) in the patent "Preparation and Application of Photocatalyst Ag/AgBr" (CN106111166A). The Ag/AgBr photocatalyst was prepared hydrothermally from bromine source and precursor. It is worth pointing out that ionic liquids will strongly absorb moisture in the air (even hydrophobic ionic liquids), greatly reducing its performance; and in practical experiments, ionic liquids are expensive and low in purity (limited by the preparation process), once mixed with Impurities will also affect its performance, limiting its practical application ability.
2015年王永强等人在专利《可见光催化剂AgBr/Ag多孔复合微球的制备方法》(CN104815679A)中使用CuBr微球为模板,采用离子交换法制备出AgBr/Ag多孔复合微球可见光催化剂。在加上400nm的滤光片氙灯(500W)照射下,对30mL的10mg/mL的甲基橙的降解率达到90%以上。In 2015, Wang Yongqiang et al. used CuBr microspheres as templates in the patent "Preparation Method of Visible Light Catalyst AgBr/Ag Porous Composite Microspheres" (CN104815679A), and prepared AgBr/Ag porous composite microspheres visible light catalyst by ion exchange method. Under the irradiation of 400nm filter xenon lamp (500W), the degradation rate of 30mL of 10mg/mL methyl orange reached more than 90%.
2018年宋彩霞等人在专利《一种Ag/ZnO纳米棒自组装体的制备方法》(CN108745354A)中采用喷雾干燥法制备Ag/ZnO纳米棒自组装体前驱体,再经焙烧得到Ag/ZnO纳米棒分级结构自组装体。制备的Ag/ZnO纳米棒组装体光催化材料用于光催化分解水制氢产率可以高达1.07mmol/g-1h-1。In 2018, Song Caixia et al. used the spray drying method to prepare the Ag/ZnO nanorod self-assembly precursor in the patent "A preparation method of Ag/ZnO nanorod self-assembly" (CN108745354A), and then calcined to obtain Ag/ZnO Nanorod Hierarchical Self-Assembly. The prepared Ag/ZnO nanorod assembly photocatalytic material can be used for photocatalytic water splitting to produce hydrogen, and the yield can be as high as 1.07mmol/g -1 h -1 .
2018年赵敬忠等人在专利《一种制备Ag负载ZnO纳米棒阵列的方法》(CN108970612A)中,首先制备ZnO种子层衬底,其次制备ZnO纳米棒阵列薄膜,最后将制备得到ZnO纳米棒阵列薄膜进行Ag负载,得到Ag负载ZnO材料。In 2018, in the patent "A Method for Preparing Ag-loaded ZnO Nanorod Arrays" (CN108970612A), Zhao Jingzhong et al. first prepared the ZnO seed layer substrate, secondly prepared the ZnO nanorod array film, and finally prepared the ZnO nanorod array film. Ag-supported to obtain an Ag-supported ZnO material.
2017年蔡凡朋等人在专利《一种中空ZnO的制备方法》(CN108002425A)中采用气相法中的喷雾热分解法制备出ZnO光催化材料。值得一提的是,该方法制备出的中空ZnO材料碎裂严重、粒径不均匀、形貌不统一。这一结果将会直接导致材料光催化活性的不可控。In 2017, Cai Fanpeng et al. used the spray thermal decomposition method in the gas phase method to prepare the ZnO photocatalytic material in the patent "A Preparation Method of Hollow ZnO" (CN108002425A). It is worth mentioning that the hollow ZnO material prepared by this method has serious fragmentation, non-uniform particle size and non-uniform morphology. This result will directly lead to the uncontrollable photocatalytic activity of the material.
2018年邢彦军等人在专利《一种常压低温条件下形貌可控微纳米ZnO的制备方法》(CN108275713A)中在常压低温条件下制备出多种形貌的微纳米ZnO。值得指出的是,这一制备方法使用到了油胺这一溶剂,众所周知,油胺具有刺激性气味,会对皮肤有灼伤和腐蚀。这一制备方法的安全生产性有待考察。In 2018, Xing Yanjun et al. prepared micro-nano ZnO with various morphologies under normal pressure and low temperature conditions in the patent "A method for preparing micro-nano ZnO with controllable morphology under normal pressure and low temperature conditions" (CN108275713A). It is worth pointing out that this preparation method uses the solvent oleylamine, which is known to have a pungent odor and can burn and corrode the skin. The safety and productivity of this preparation method needs to be investigated.
尽管上述方法在制备光催化材料方面做出了突出的贡献,然而这些制备方法存着很多共性的问题,如:制备过程繁琐、原料要求苛刻和得到的特殊形貌催化剂的催化性能不强。相比较而言,本发明使用的一步水热法工艺简单、操作方便、各参数容易控制、原料价廉易得、催化剂的特殊形貌有益于催化活性的提升。并且CTAB除了作为表面活性剂控制形貌外,还充当了溴源,控制了形貌,节省了原料,一举两得。Although the above methods have made outstanding contributions to the preparation of photocatalytic materials, these preparation methods have many common problems, such as cumbersome preparation process, harsh raw material requirements, and poor catalytic performance of the obtained catalysts with special morphology. Comparatively speaking, the one-step hydrothermal method used in the present invention has simple process, convenient operation, easy control of various parameters, cheap and easy-to-obtain raw materials, and the special morphology of the catalyst is beneficial to the improvement of catalytic activity. In addition to controlling the morphology as a surfactant, CTAB also acts as a bromine source, controlling the morphology and saving raw materials, killing two birds with one stone.
综上所述,本发明中通过简单的一步水热法,合成了光催化性能优异的花状Ag@AgBr/ZnO材料,符合实际应用中对材料的相关要求。To sum up, in the present invention, a flower-like Ag@AgBr/ZnO material with excellent photocatalytic performance is synthesized by a simple one-step hydrothermal method, which meets the relevant requirements for materials in practical applications.
发明内容SUMMARY OF THE INVENTION
本发明的目的是为了解决现有Ag@AgBr/ZnO光催化材料的制备方法存在的原料价格贵、工艺流程复杂繁琐、制备时间长、生产效率不适合批量化生产,以及光催化剂光催化活性较差等问题,提供了一种花状的Ag@AgBr/ZnO光催化材料的制备方法。The purpose of the present invention is to solve the problems of expensive raw materials, complicated and tedious technological process, long preparation time, unsuitable production efficiency for mass production, and relatively high photocatalytic activity of the existing Ag@AgBr/ZnO photocatalytic material preparation methods. To solve the problem of poor quality, a preparation method of flower-like Ag@AgBr/ZnO photocatalytic material is provided.
花状的Ag@AgBr/ZnO光催化材料的制备方法按照以下步骤进行:The preparation method of flower-like Ag@AgBr/ZnO photocatalytic material is carried out according to the following steps:
一、按Zn元素、Ag元素、六亚甲基四胺和表面活性剂的物质的量之比为一定值,配置一定浓度的Zn源和表面活性剂于30mL蒸馏水中,得到Zn源溶液;配置一定浓度的Ag源和六亚甲基四胺于20mL蒸馏水中,并加入氧化剂,得到Ag源溶液;1. According to the ratio of the amount of Zn element, Ag element, hexamethylenetetramine and surfactant to a certain value, configure a certain concentration of Zn source and surfactant in 30 mL of distilled water to obtain a Zn source solution; configure A certain concentration of Ag source and hexamethylenetetramine are dissolved in 20 mL of distilled water, and an oxidant is added to obtain an Ag source solution;
二、将Ag源溶液以一定的滴加速率逐滴加入到Zn源溶液中,将混合溶液转移至高压反应釜进行水热反应,混合溶液约占反应釜容积的50%,以一定的水热温度维持一定的水热时间。2. Add the Ag source solution dropwise to the Zn source solution at a certain drop rate, and transfer the mixed solution to the high-pressure reactor for hydrothermal reaction. The mixed solution accounts for about 50% of the volume of the reactor. The temperature is maintained for a certain hydrothermal time.
三、将生成物经水洗、醇洗和烘干后,移入马弗炉,在空气氛围下以一定温度煅烧一定的时间,冷却至室温后得到花状形貌的Ag@AgBr/ZnO光催化材料。3. After washing with water, alcohol and drying, the product was transferred into a muffle furnace, calcined at a certain temperature for a certain period of time in an air atmosphere, and cooled to room temperature to obtain a flower-like Ag@AgBr/ZnO photocatalytic material .
步骤一中所述的Zn元素、Ag元素、六亚甲基四胺和表面活性剂的物质的量之比为1:(0.01~0.4):1:(0.1~1)。The material ratio of Zn element, Ag element, hexamethylenetetramine and surfactant described in
步骤一中所述的Zn源、表面活性剂、Ag源和六亚甲基四胺的浓度分别为0.3333mol/L、(0.03333~0.3333)mol/L、(0.05~0.2)mol/L和0.5mol/L。The concentrations of the Zn source, surfactant, Ag source and hexamethylenetetramine described in
步骤一中所述的Zn源是硫酸锌(ZnSO4)、二水合醋酸锌(C4H6O4Zn·2H2O)、六水合硝酸锌(Zn(NO3)2·6H2O)或七水合硫酸锌(ZnSO4·7H2O)化合物。The Zn source described in
步骤一中所述的表面活性剂为十六烷基三甲基溴化铵(CTAB)The surfactant described in
步骤一中所述的氧化剂为H2O2(30%)。 The oxidant described in step one is H2O2 ( 30%).
步骤二中所述的滴加速率为1~3秒/滴;设定的水热温度为100~180℃;水热时间1~5小时。The dropping acceleration rate described in step 2 is 1-3 seconds/drop; the set hydrothermal temperature is 100-180°C; and the hydrothermal time is 1-5 hours.
步骤三中所述的煅烧温度为500~800℃;煅烧时间为1~3h。The calcination temperature in step 3 is 500-800°C; the calcination time is 1-3h.
本发明的有益效果如下:The beneficial effects of the present invention are as follows:
本发明采用锌盐和硝酸银作为银源,使原料成分达到分子水平混合,合成的由多孔片层组成的花状Ag@AgBr/ZnO光催化材料化学组分均匀;本发明采用CTAB作为表面活性剂,能有效控制催化剂的形貌和粒径,使合成得到的花状Ag@AgBr/ZnO光催化材料具有统一的形貌和均匀的粒径;同时,CTAB还作为Br源参与反应,无需额外选择其他Br源,节约成本,有效降低了Ag@AgBr/ZnO光催化剂的制备难度,制备出的由多孔片组成的花状Ag@AgBr/ZnO具有极强的光催化活性,符合实际应用中对材料的相关要求。The invention adopts zinc salt and silver nitrate as the silver source, so that the raw material components are mixed at the molecular level, and the synthesized flower-shaped Ag@AgBr/ZnO photocatalytic material composed of porous sheets has uniform chemical components; the invention adopts CTAB as the surface active material It can effectively control the morphology and particle size of the catalyst, so that the synthesized flower-like Ag@AgBr/ZnO photocatalytic material has a uniform morphology and uniform particle size; at the same time, CTAB also participates in the reaction as a Br source, without additional Selecting other Br sources saves costs and effectively reduces the difficulty of preparing Ag@AgBr/ZnO photocatalysts. The prepared flower-like Ag@AgBr/ZnO composed of porous sheets has extremely strong photocatalytic activity, which is in line with practical applications. material requirements.
附图说明Description of drawings
图1、采用本发明方法制备的花状Ag@AgBr/ZnO材料的SEM照片Fig. 1, the SEM photograph of the flower-shaped Ag@AgBr/ZnO material prepared by the method of the present invention
图2、采用本发明方法制备的花状Ag@AgBr/ZnO材料的XRD谱图Fig. 2, the XRD spectrum of the flower-like Ag@AgBr/ZnO material prepared by the method of the present invention
图3、采用本发明方法制备的花状Ag@AgBr/ZnO材料(具体实施方式一)对罗丹明B的降解效率与光催化时间的关系曲线,催化剂量1g·L-1,罗丹明B浓度5mg·L-1。图中(a)Ag@AgBr/ZnO材料(具体实施方式一)在模拟太阳光下催化时罗丹明B的降解效率;(b)不使用Ag@AgBr/ZnO材料催化时在模拟太阳光下罗丹明B的自然降解效率;(c)Ag@AgBr/ZnO材料(具体实施方式一)在无光条件下催化时罗丹明B的降解效率。Fig. 3. The relationship curve of the degradation efficiency of Rhodamine B and the photocatalytic time of the flower-shaped Ag@AgBr/ZnO material (specific embodiment 1) prepared by the method of the present invention, the catalyst amount is 1 g·L -1 , the Rhodamine B concentration 5mg·L -1 . In the figure (a) Ag@AgBr/ZnO material (specific embodiment 1) degradation efficiency of Rhodamine B when catalyzed under simulated sunlight; (b) Rhodamine B under simulated sunlight without Ag@AgBr/ZnO material catalysis The natural degradation efficiency of Ming B; (c) the degradation efficiency of rhodamine B when the Ag@AgBr/ZnO material (specific embodiment 1) is catalyzed under no-light conditions.
图4、采用本发明方法制备的花状Ag@AgBr/ZnO材料(具体实施方式一)亚甲基蓝的降解效率与光催化时间的关系曲线,催化剂量1g·L-1,亚甲基蓝浓度10mg·L-1。Fig. 4. The relationship curve between the degradation efficiency of methylene blue and the photocatalytic time of the flower-shaped Ag@AgBr/ZnO material (specific embodiment 1) prepared by the method of the present invention, the catalyst amount is 1 g·L -1 , and the methylene blue concentration is 10 mg·L -1 .
图5、采用本发明方法制备的花状Ag@AgBr/ZnO材料(具体实施方式一)头孢呋辛钠的降解效率与光催化时间的关系曲线,催化剂量1g·L-1,头孢呋辛钠浓度20mg·L-1。Fig. 5, the relation curve of the degradation efficiency of cefuroxime sodium and the photocatalytic time of the flower-shaped Ag@AgBr/ZnO material prepared by the method of the present invention (specific embodiment 1), the catalyst amount is 1 g·L -1 , the cefuroxime sodium The concentration is 20mg·L -1 .
具体实施方式Detailed ways
本发明技术方案不局限于以下所列举具体实施方式,还包括各具体实施方式间的任意组合。The technical solutions of the present invention are not limited to the specific embodiments listed below, but also include any combination of specific embodiments.
具体实施方式一:本实施方式中花状的Ag@AgBr/ZnO材料光催化材料的制备方法按照以下步骤进行:Embodiment 1: The preparation method of the flower-shaped Ag@AgBr/ZnO material photocatalytic material in this embodiment is carried out according to the following steps:
一、按Zn元素、Ag元素、六亚甲基四胺和表面活性剂的物质的量之比为1:0.2:1:0.55的比例称取二水合乙酸锌、硝酸银、六亚甲基四胺和CTAB,配置0.3333mol/L和0.1833mol/L的Zn源和表面活性剂于30mL蒸馏水中,得到Zn源溶液;配置0.1mol/L和0.5mol/L的Ag源和六亚甲基四胺于20mL蒸馏水中,并加入氧化剂,Ag源溶液;1. Weigh zinc acetate dihydrate, silver nitrate, hexamethylenetetramine in the ratio of 1:0.2:1:0.55 according to the ratio of Zn element, Ag element, hexamethylenetetramine and surfactant. Amine and CTAB, configure 0.3333mol/L and 0.1833mol/L Zn source and surfactant in 30mL distilled water to obtain Zn source solution; configure 0.1mol/L and 0.5mol/L Ag source and hexamethylenetetramine Amine in 20mL of distilled water, and add oxidant, Ag source solution;
二、将Ag源溶液以1秒/滴的滴加速率逐滴加入到Zn源溶液中,将混合溶液转移至高压反应釜进行水热反应,混合溶液约占反应釜容积的50%,设定的水热温度为140℃,并在该温度下维持水热时间3小时;2. The Ag source solution is added dropwise to the Zn source solution at a drop rate of 1 second/drop, and the mixed solution is transferred to a high-pressure reactor for hydrothermal reaction. The mixed solution accounts for about 50% of the volume of the reactor. The hydrothermal temperature is 140°C, and the hydrothermal time is maintained at this temperature for 3 hours;
三、将生成物经水洗、醇洗和烘干后,移入马弗炉,在空气氛围下以650℃温度煅烧2h,冷却至室温后得到花状Ag@AgBr/ZnO光催化材料。3. After washing with water, alcohol and drying, the resultant was transferred into a muffle furnace, calcined at 650 °C for 2 h in an air atmosphere, and cooled to room temperature to obtain a flower-shaped Ag@AgBr/ZnO photocatalytic material.
本实施方式的有益效果如下:本实施方式合成的花状Ag@AgBr/ZnO材料具有由多孔片层成簇组成的花状结构,使用CTAB能有效地控制催化剂晶体的生长方向和团簇方式,使其形貌呈现为:由多孔片层成簇组装成的花状,花状的Ag@AgBr/ZnO材料直径约为4-6μm,如图1所示。较大的尺寸有利于光催化剂光催化过程中的自由电子转移,XRD的结果(图2)显示出本发明制备的复合材料的高结晶性质,这一特性同样有利于光催化剂光催化过程中的自由电子转移。自由电子的高效传输能够在一定程度上减少电子空穴的复合几率,使Ag@AgBr/ZnO复合光催化材料体现出极其优异的光催化活性。The beneficial effects of this embodiment are as follows: the flower-like Ag@AgBr/ZnO material synthesized in this embodiment has a flower-like structure composed of clusters of porous lamellae, and the use of CTAB can effectively control the growth direction and clustering mode of catalyst crystals, The morphology of the Ag@AgBr/ZnO material is about 4-6 μm in diameter, as shown in Figure 1. The larger size is beneficial to the free electron transfer in the photocatalytic process of the photocatalyst, and the XRD result (Fig. 2) shows the high crystalline nature of the composite material prepared by the present invention, which is also beneficial to the photocatalyst in the photocatalytic process. free electron transfer. The efficient transport of free electrons can reduce the recombination probability of electron holes to a certain extent, so that the Ag@AgBr/ZnO composite photocatalytic material exhibits extremely excellent photocatalytic activity.
用制备的花状Ag@AgBr/ZnO材料1g·L-1降解5mg·L-1的罗丹明B溶液,模拟太阳光下搅拌30min,降解率达到99.11%。A 5 mg·L -1 solution of Rhodamine B was degraded with 1 g·L -1 of the prepared flower-like Ag@AgBr/ZnO material, and stirred for 30 min under simulated sunlight, and the degradation rate reached 99.11%.
用制备的花状Ag@AgBr/ZnO材料1g·L-1降解10mg·L-1的亚甲基蓝溶液,模拟太阳光下搅拌30min,降解率达到99.99%。10 mg·L -1 of methylene blue solution was degraded with 1 g·L -1 of the prepared flower-like Ag@AgBr/ZnO material, and stirred for 30 min under simulated sunlight, and the degradation rate reached 99.99%.
用制备的花状Ag@AgBr/ZnO材料1g·L-1降解20mg·L-1的头孢呋辛钠溶液,模拟太阳光下搅拌30min,降解率为74.77%;搅拌150min,降解率达到95.09%。1 g·L -1 of the prepared flower-like Ag@AgBr/ZnO material was used to degrade 20 mg·L -1 of cefuroxime sodium solution, and stirred for 30 min under simulated sunlight, and the degradation rate was 74.77%; after stirring for 150 min, the degradation rate reached 95.09% .
具体实施方式二:Specific implementation two:
一、按Zn元素、Ag元素、六亚甲基四胺和表面活性剂的物质的量之比为1:0.2:1:0.55的比例称取二水合乙酸锌、硝酸银、六亚甲基四胺和CTAB,配置0.3333mol/L和0.1833mol/L的Zn源和表面活性剂于30mL蒸馏水中,得到Zn源溶液;配置0.1mol/L和0.5mol/L的Ag源和六亚甲基四胺于20mL蒸馏水中,并加入氧化剂,Ag源溶液;1. Weigh zinc acetate dihydrate, silver nitrate, hexamethylenetetramine in the ratio of 1:0.2:1:0.55 according to the ratio of Zn element, Ag element, hexamethylenetetramine and surfactant. Amine and CTAB, configure 0.3333mol/L and 0.1833mol/L Zn source and surfactant in 30mL distilled water to obtain Zn source solution; configure 0.1mol/L and 0.5mol/L Ag source and hexamethylenetetramine Amine in 20mL of distilled water, and add oxidant, Ag source solution;
二、将Ag源溶液以3秒/滴的滴加速率逐滴加入到Zn源溶液中,将混合溶液转移至高压反应釜进行水热反应,混合溶液约占反应釜容积的50%,设定的水热温度为160℃,并在该温度下维持水热时间2.5小时;2. The Ag source solution is added dropwise to the Zn source solution at a drop rate of 3 seconds/drop, and the mixed solution is transferred to a high-pressure reactor for hydrothermal reaction. The mixed solution accounts for about 50% of the volume of the reactor. The hydrothermal temperature is 160℃, and the hydrothermal time is maintained at this temperature for 2.5 hours;
三、将生成物经水洗、醇洗和烘干后,移入马弗炉,在空气氛围下以500℃温度煅烧2.5h,冷却至室温后得到花状Ag@AgBr/ZnO光催化材料。3. After washing with water, alcohol and drying, the resultant was transferred into a muffle furnace, calcined at 500 °C for 2.5 h in an air atmosphere, and cooled to room temperature to obtain a flower-shaped Ag@AgBr/ZnO photocatalytic material.
具体实施方式三:Specific implementation three:
一、按Zn元素、Ag元素、六亚甲基四胺和表面活性剂的物质的量之比为1:0.2:1:0.55的比例称取二水合乙酸锌、硝酸银、六亚甲基四胺和CTAB,配置0.3333mol/L和0.1833mol/L的Zn源和表面活性剂于30mL蒸馏水中,得到Zn源溶液;配置0.1mol/L和0.5mol/L的Ag源和六亚甲基四胺于20mL蒸馏水中,并加入氧化剂,Ag源溶液;1. Weigh zinc acetate dihydrate, silver nitrate, hexamethylenetetramine in the ratio of 1:0.2:1:0.55 according to the ratio of Zn element, Ag element, hexamethylenetetramine and surfactant. Amine and CTAB, configure 0.3333mol/L and 0.1833mol/L Zn source and surfactant in 30mL distilled water to obtain Zn source solution; configure 0.1mol/L and 0.5mol/L Ag source and hexamethylenetetramine Amine in 20mL of distilled water, and add oxidant, Ag source solution;
二、将Ag源溶液以2秒/滴的滴加速率逐滴加入到Zn源溶液中,将混合溶液转移至高压反应釜进行水热反应,混合溶液约占反应釜容积的50%,设定的水热温度为130℃,并在该温度下维持水热时间4小时;2. The Ag source solution is added dropwise to the Zn source solution at a drop rate of 2 seconds/drop, and the mixed solution is transferred to a high-pressure reactor for hydrothermal reaction. The mixed solution accounts for about 50% of the volume of the reactor. The hydrothermal temperature is 130°C, and the hydrothermal time is maintained at this temperature for 4 hours;
三、将生成物经水洗、醇洗和烘干后,移入马弗炉,在空气氛围下以700℃温度煅烧3h,冷却至室温后得到花状Ag@AgBr/ZnO光催化材料。3. After washing with water, alcohol and drying, the product was transferred into a muffle furnace, calcined at 700 °C for 3 h in an air atmosphere, and cooled to room temperature to obtain a flower-shaped Ag@AgBr/ZnO photocatalytic material.
本发明所示的花状Ag@AgBr/ZnO粉末可用于光催化分解有机污染物,以太阳光或紫外光为光源。光催化反应时,在搅拌情况下进行,加入一定量催化剂(0.5~1g/L),在一定时间内(0.5~3h),降解一定浓度(5~20mg/L)的罗丹明B、亚甲基蓝和头孢呋辛钠等有机污染物的水溶液。例如:催化降解5mg/L罗丹明B溶液,取100ml罗丹明B溶液,加入催化剂(0.5~1g/L),在太阳光或紫外光下进行催化反应,每隔一段时间(7.5~30min),取样3~5ml溶液样品,过滤后,用紫外-可见分光光度计测定溶液的吸光度来检测溶液浓度的变化,从而计算出有机污染物的降解率。The flower-shaped Ag@AgBr/ZnO powder shown in the invention can be used for photocatalytic decomposition of organic pollutants, and sunlight or ultraviolet light is used as a light source. During the photocatalytic reaction, it is carried out under stirring, adding a certain amount of catalyst (0.5-1g/L), and degrading a certain concentration (5-20mg/L) of Rhodamine B, methylene blue and rhodamine within a certain time (0.5-3h). Aqueous solutions of organic pollutants such as cefuroxime sodium. For example: to catalytically degrade 5mg/L Rhodamine B solution, take 100ml Rhodamine B solution, add catalyst (0.5~1g/L), carry out catalytic reaction under sunlight or ultraviolet light, at regular intervals (7.5~30min), Sampling 3-5ml of solution sample, after filtration, measure the absorbance of the solution with an ultraviolet-visible spectrophotometer to detect the change of solution concentration, thereby calculating the degradation rate of organic pollutants.
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