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CN114797906A - BiOCl @ Bi 2 S 3 In-situ synthesis method and application of composite material - Google Patents

BiOCl @ Bi 2 S 3 In-situ synthesis method and application of composite material Download PDF

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CN114797906A
CN114797906A CN202110108476.7A CN202110108476A CN114797906A CN 114797906 A CN114797906 A CN 114797906A CN 202110108476 A CN202110108476 A CN 202110108476A CN 114797906 A CN114797906 A CN 114797906A
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CN114797906B (en
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兰东辉
陈琨
李薇
易兵
沈静
邓人杰
陈镇
伍水生
区泽堂
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Hunan Institute of Engineering
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
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    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/10Heat treatment in the presence of water, e.g. steam
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/343Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the pharmaceutical industry, e.g. containing antibiotics
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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Abstract

The invention discloses BiOCl @ Bi 2 S 3 The in-situ synthesis method of the composite material and the application thereof comprise the following steps: (1) dissolving a bismuth source in an alcohol solution to obtain a solution A; (2) mixing vitamin B 1 Dissolving hydrochloride in water to obtain a solution B, and then adding the solution B into the solution A under stirring to obtain a mixed solution C; (3) carrying out hydrothermal treatment on the mixed solution C, and carrying out solid-liquid separation, washing and drying to obtain the BiOCl @ Bi 2 S 3 A composite material. The invention uses vitamin B 1 The hydrochloride is used as a chlorine source and a sulfur source and is used as a surfactant, and vitamin B is added after bismuth oxychloride is generated 1 The in-situ etching of the sulfur source decomposed by the hydrochloride is beneficial to BiOCl and Bi 2 S 3 Heterojunction is compositely constructed, separation of photoproduction electrons and holes is promoted, degradation of antibiotics and volatile organic pollutants (VOCs) can be efficiently catalyzed under the condition of visible light, and activity of the catalyst is almost unchanged after the catalyst is recycled for many times.

Description

一种BiOCl@Bi2S3复合材料的原位合成方法及其应用A kind of in situ synthesis method of BiOCl@Bi2S3 composite and its application

技术领域technical field

本发明属于材料制备和环境保护技术领域,具体涉及一种BiOCl@Bi2S3复合材料的原位合成方法及其在可见光催化抗生素降解和VOCs降解中的应用。The invention belongs to the technical field of material preparation and environmental protection, and in particular relates to an in-situ synthesis method of a BiOCl@Bi 2 S 3 composite material and its application in visible light catalyzed antibiotic degradation and VOCs degradation.

背景技术Background technique

采用可见光催化技术,通过半导体光催化材料直接利用太阳能将环境中有毒有害有机污染物实现完全矿化降解,是一项低成本的绿色共性技术,在环境保护领域具有良好的应用前景。而可见光催化技术的关键是高效和稳定半导体催化剂的研制。目前半导体光催化剂主要存在以下问题:(1)部分半导体材料对光的吸收效率不高,仅能吸收紫外光(仅占太阳光能量的4%);(2)光生空穴和电子易复合,其分离效率低;(3)光催化剂的制备过程复杂,需要引入有毒有害溶剂或者结构导向剂;(4)光催化剂难以实现规模化生产等。因此,开发绿色、简单、容易规模化生产的光催化剂合成方法,制备高效、稳定的可见光催化剂具有重要的意义。Visible light catalysis technology is used to completely mineralize and degrade toxic and harmful organic pollutants in the environment by directly utilizing solar energy through semiconductor photocatalytic materials. It is a low-cost green general technology and has good application prospects in the field of environmental protection. The key to visible light catalysis technology is the development of efficient and stable semiconductor catalysts. At present, semiconductor photocatalysts mainly have the following problems: (1) Some semiconductor materials have low light absorption efficiency, and can only absorb ultraviolet light (only 4% of the energy of sunlight); (2) Photogenerated holes and electrons are easy to recombine, The separation efficiency is low; (3) the preparation process of the photocatalyst is complicated, and toxic and harmful solvents or structure-directing agents need to be introduced; (4) the photocatalyst is difficult to achieve large-scale production. Therefore, it is of great significance to develop a green, simple, and easy-to-scale photocatalyst synthesis method to prepare efficient and stable visible light catalysts.

BiOCl和Bi2S3材料均具有层状结构,其禁带宽度分别为3.0~3.5eV和1.3~1.7eV。BiOCl禁带宽度较大通常只能在紫外光区具有较好的光催化活性。Bi2S3禁带宽度较窄,是一种潜在的对可见光响应的光催化剂,但由于其价带和导带位置比较近,光生电子-空穴复合率高,一般需要与其它材料复合才表现出较好的催化活性。有文献报道将BiOCl和Bi2S3复合构建异质结,不仅有利于提高可见光吸收,有利于光生电子和空穴的产生,还可促进光生电子和空穴的分离,提高光催化性能。Both BiOCl and Bi 2 S 3 materials have a layered structure, and their forbidden band widths are 3.0-3.5 eV and 1.3-1.7 eV, respectively. BiOCl has a large forbidden band width and usually only has better photocatalytic activity in the ultraviolet region. Bi 2 S 3 has a narrow band gap and is a potential photocatalyst that responds to visible light. However, due to its relatively close valence band and conduction band, the photogenerated electron-hole recombination rate is high, and it generally needs to be recombined with other materials. showed good catalytic activity. It has been reported in the literature that BiOCl and Bi 2 S 3 are composited to construct a heterojunction, which is not only beneficial to improve the absorption of visible light and the generation of photogenerated electrons and holes, but also to promote the separation of photogenerated electrons and holes and improve the photocatalytic performance.

目前合成BiOCl和Bi2S3复合材料,一般是先通过水解法、水(溶剂)热法、醇热法、软模板法、高温固相法和反相微乳法等制备BiOCl,再用硫源进行刻蚀,合成过程较复杂,且一般需要加入酸或者碱以及表面活性剂。At present, the synthesis of BiOCl and Bi 2 S 3 composite materials is generally carried out by hydrolysis, water (solvent) thermal method, alcohol thermal method, soft template method, high temperature solid phase method and inverse microemulsion method. The source is etched, and the synthesis process is complicated, and generally needs to add acid or alkali and surfactant.

发明内容SUMMARY OF THE INVENTION

为了解决现有技术中存在的问题,本发明的目的是在于提供一种BiOCl@Bi2S3复合材料的原位合成方法,以维生素B1盐酸盐作为氯源和硫源,同时作为表面活性剂,在生成氯氧化铋后被维生素B1盐酸盐分解的硫源原位刻蚀,有利于BiOCl和Bi2S3复合构建异质结,促进光生电子和空穴的分离,在可见光条件下,可高效催化抗生素和易挥发有机污染物(VOCs)降解,且催化剂多次循环使用后活性几乎不变。In order to solve the problems existing in the prior art, the purpose of the present invention is to provide a method for in-situ synthesis of BiOCl@Bi 2 S 3 composite materials, using vitamin B 1 hydrochloride as a chlorine source and a sulfur source, and simultaneously as a surface The active agent, after the formation of bismuth oxychloride, is etched in situ by the sulfur source decomposed by vitamin B1 hydrochloride, which is conducive to the composite construction of BiOCl and Bi2S3 to build a heterojunction, and promotes the separation of photogenerated electrons and holes, which can be used in visible light. Under the same conditions, the degradation of antibiotics and volatile organic pollutants (VOCs) can be efficiently catalyzed, and the activity of the catalyst is almost unchanged after repeated use.

为解决上述问题,本发明采用的技术方案为:For solving the above problems, the technical scheme adopted in the present invention is:

一种BiOCl@Bi2S3复合材料的原位合成方法,包括如下步骤:An in-situ synthesis method of BiOCl@Bi 2 S 3 composite material, comprising the following steps:

(1)将铋源溶于醇溶液,得溶液A;(1) bismuth source is dissolved in alcohol solution to obtain solution A;

(2)将维生素B1盐酸盐溶于水中得溶液B,随后在搅拌下将溶液B加入至溶液A中,得到混合液C;(2) dissolving vitamin B 1 hydrochloride in water to obtain solution B, then adding solution B to solution A under stirring to obtain mixed solution C;

(3)将混合液C进行水热处理,经固液分离、洗涤、干燥即得所述BiOCl@Bi2S3复合材料。(3) The mixed solution C is subjected to hydrothermal treatment, and the BiOCl@Bi 2 S 3 composite material is obtained through solid-liquid separation, washing and drying.

优选的,步骤(1)中,所述铋源选自五水硝酸铋、氯化铋、柠檬酸铋中的一种或几种。Preferably, in step (1), the bismuth source is selected from one or more of bismuth nitrate pentahydrate, bismuth chloride and bismuth citrate.

优选的,步骤(1)中,所述醇选自甲醇、乙醇、异丙醇、乙二醇、丙三醇中的一种或几种。Preferably, in step (1), the alcohol is selected from one or more of methanol, ethanol, isopropanol, ethylene glycol, and glycerol.

优选的,步骤(1)中,所述溶液A中,铋源的浓度为0.05~0.2mol/L。Preferably, in step (1), in the solution A, the concentration of the bismuth source is 0.05-0.2 mol/L.

优选的,步骤(2)中,所述溶液B中,维生素B1盐酸盐的浓度为0.1~0.5mol/L。Preferably, in step (2), in the solution B, the concentration of vitamin B 1 hydrochloride is 0.1-0.5 mol/L.

优选的,步骤(2)中,所述铋源和维生素B1盐酸盐的摩尔比为1~5:1,。Preferably, in step (2), the molar ratio of the bismuth source and vitamin B 1 hydrochloride is 1-5:1.

优选的,步骤(3)中,水热处理的温度为80~160℃,时间为6~24h。Preferably, in step (3), the temperature of the hydrothermal treatment is 80-160° C., and the time is 6-24 h.

本发明还提供了上述合成的BiOCl@Bi2S3复合材料的应用,将其作为可见光下抗生素或VOCs降解的光催化剂;The invention also provides the application of the synthesized BiOCl@Bi 2 S 3 composite material as a photocatalyst for the degradation of antibiotics or VOCs under visible light;

具体步骤为:室温下,将BiOCl@Bi2S3复合材料加入到抗生素浓度为15~150mg/L的水中或VOCs浓度为0.2~2mg/L的气体中,反应0.1~12h即可。The specific steps are as follows: at room temperature, the BiOCl@Bi 2 S 3 composite material is added to water with an antibiotic concentration of 15-150 mg/L or gas with a VOCs concentration of 0.2-2 mg/L, and the reaction is sufficient for 0.1-12 h.

优选的,所述抗生素选自环丙沙星、诺氟沙星、氧氟沙星、四环素、磺胺甲恶唑、磺胺二甲基嘧啶和土霉素中的一种或多种,所述BiOCl@Bi2S3复合材料与抗生素的质量比为1:0.01~0.1。Preferably, the antibiotic is selected from one or more of ciprofloxacin, norfloxacin, ofloxacin, tetracycline, sulfamethoxazole, sulfamethazine and oxytetracycline, and the BiOCl The mass ratio of @Bi 2 S 3 composites to antibiotics is 1:0.01~0.1.

优选的,所述VOCs选自甲醛、甲苯、苯和二甲苯中的一种或多种,所述BiOCl@Bi2S3复合材料与VOCs的质量比为1:0.005~0.05。Preferably, the VOCs are selected from one or more of formaldehyde, toluene, benzene and xylene, and the mass ratio of the BiOCl@Bi 2 S 3 composite material to the VOCs is 1:0.005-0.05.

与现有技术相比,本发明的技术效果为:Compared with the prior art, the technical effect of the present invention is:

1、本发明中维生素B1盐酸盐既作为氯源和硫源,又作为表面活性剂,有利于形成均一结构且避免使用酸、碱以及表面活性剂。1. In the present invention, vitamin B 1 hydrochloride is used as both a chlorine source and a sulfur source, and also as a surfactant, which is conducive to the formation of a uniform structure and avoids the use of acids, alkalis and surfactants.

2、本发明采用原位合成方法,在生成氯氧化铋后被维生素B1盐酸盐分解的硫源原位刻蚀,有利于构建异质结,促进光生电子和空穴的分离。2. The present invention adopts an in-situ synthesis method, and after the bismuth oxychloride is generated, it is etched in-situ by a sulfur source decomposed by vitamin B 1 hydrochloride, which is conducive to the construction of a heterojunction and promotes the separation of photogenerated electrons and holes.

3、本发明中的BiOCl@Bi2S3复合材料可在可见光下高效催化抗生素和VOCs降解,且催化材料可以循环使用。3. The BiOCl@Bi 2 S 3 composite material in the present invention can efficiently catalyze the degradation of antibiotics and VOCs under visible light, and the catalytic material can be recycled.

具体实施方式Detailed ways

为了使本发明的目的、技术方案及优点更加清楚明白,下面结合具体实施例对本发明作进一步详细说明。应当理解,此处所描述的具体实施例仅用以解释本发明,并不用于限定本发明。In order to make the objectives, technical solutions and advantages of the present invention clearer, the present invention will be further described in detail below with reference to specific embodiments. It should be understood that the specific embodiments described herein are only used to explain the present invention, but not to limit the present invention.

实施例1Example 1

室温下,称取5mmol五水硝酸铋溶于100mL乙二醇溶液,得溶液A;将5mmol维生素B1盐酸盐溶于10mL水中,得溶液B;随后在搅拌下将溶液B缓慢滴加至溶液A中,得到混合液C;将混合液C置于晶化釜中密封后,160℃条件下处理6h,冷却后洗涤干燥,所得材料记为BiOCl@Bi2S3-1复合材料。At room temperature, 5mmol of bismuth nitrate pentahydrate was weighed and dissolved in 100mL of ethylene glycol solution to obtain solution A; 5mmol of vitamin B 1 hydrochloride was dissolved in 10mL of water to obtain solution B; then under stirring, solution B was slowly added dropwise to In solution A, mixed solution C was obtained; the mixed solution C was placed in a crystallization kettle and sealed, treated at 160 °C for 6 h, washed and dried after cooling, and the obtained material was denoted as BiOCl@Bi 2 S 3 -1 composite material.

实施例2Example 2

室温下,称取5mmol五水柠檬酸铋溶于50mL异丙醇溶液,得溶液A;将1mmol维生素B1盐酸盐溶于10mL水中,得溶液B;随后在搅拌下将溶液B缓慢滴加至溶液A中,得到混合液C;将混合液C置于晶化釜中密封后,105℃条件下处理12h,冷却后洗涤干燥,所得材料记为BiOCl@Bi2S3-2复合材料。At room temperature, 5mmol of bismuth citrate pentahydrate was weighed and dissolved in 50mL of isopropanol solution to obtain solution A; 1mmol of vitamin B 1 hydrochloride was dissolved in 10mL of water to obtain solution B; then solution B was slowly added dropwise under stirring into solution A to obtain mixed solution C; the mixed solution C was placed in a crystallization kettle and sealed, treated at 105 °C for 12 h, washed and dried after cooling, and the obtained material was recorded as BiOCl@Bi 2 S 3 -2 composite material.

实施例3Example 3

室温下,称取5mmol五水氯化铋溶于25mL乙醇溶液,得溶液A;将2mmol维生素B1盐酸盐溶于10mL水中,得溶液B;随后在搅拌下将溶液B缓慢滴加至溶液A中,得到混合液C;将混合液C置于晶化釜中密封后,80℃条件下处理24h,冷却后洗涤干燥,所得材料记为BiOCl@Bi2S3-3复合材料。At room temperature, 5mmol of bismuth chloride pentahydrate was weighed and dissolved in 25mL of ethanol solution to obtain solution A; 2mmol of vitamin B 1 hydrochloride was dissolved in 10mL of water to obtain solution B; then solution B was slowly added dropwise to the solution under stirring. In A, mixed solution C was obtained; the mixed solution C was placed in a crystallization kettle and sealed, treated at 80°C for 24 h, washed and dried after cooling, and the obtained material was recorded as BiOCl@Bi 2 S 3 -3 composite material.

实施例4Example 4

室温下,称取5mmol五水硝酸铋溶于50mL乙二醇溶液,得溶液A;将1.67mmol维生素B1盐酸盐溶于10mL水中,得溶液B;随后在搅拌下将溶液B缓慢滴加至溶液A中,得到混合液C;将混合液C置于晶化釜中密封后,135℃条件下处理12h,冷却后洗涤干燥,所得材料记为BiOCl@Bi2S3-4复合材料。At room temperature, 5mmol of bismuth nitrate pentahydrate was weighed and dissolved in 50mL of ethylene glycol solution to obtain solution A; 1.67mmol of vitamin B 1 hydrochloride was dissolved in 10mL of water to obtain solution B; then solution B was slowly added dropwise under stirring Put the mixed solution C into the solution A to obtain the mixed solution C; after the mixed solution C was placed in a crystallization kettle and sealed, treated at 135 °C for 12 h, washed and dried after cooling, and the obtained material was recorded as BiOCl@Bi 2 S 3 -4 composite material.

对比例1Comparative Example 1

室温下,称取5mmol五水硝酸铋溶于50mL乙二醇溶液,得溶液A;将2.5mmol维生素B1盐酸盐溶于10mL水中,得溶液B;随后在搅拌下将溶液B缓慢滴加至溶液A中,搅拌12h,冷却后洗涤干燥,所得材料记为BiOCl。At room temperature, 5mmol of bismuth nitrate pentahydrate was weighed and dissolved in 50mL of ethylene glycol solution to obtain solution A; 2.5mmol of vitamin B 1 hydrochloride was dissolved in 10mL of water to obtain solution B; then solution B was slowly added dropwise under stirring into solution A, stirred for 12 h, washed and dried after cooling, and the obtained material was designated as BiOCl.

对比例2Comparative Example 2

室温下,称取5mmol五水硝酸铋溶于50mL乙二醇溶液,得溶液A;将10mmolNa2S溶于30mL水中,得溶液B;随后在搅拌下将溶液B缓慢滴加至溶液A中,搅拌12h,冷却后洗涤干燥,所得材料记为Bi2S3At room temperature, 5mmol of bismuth nitrate pentahydrate was weighed and dissolved in 50 mL of ethylene glycol solution to obtain solution A; 10 mmol of Na 2 S was dissolved in 30 mL of water to obtain solution B; then solution B was slowly added dropwise to solution A under stirring, Stirred for 12 h, washed and dried after cooling, and the obtained material was designated as Bi 2 S 3 .

对比例3Comparative Example 3

称取对比例1制备的1.3g BiOCl(5mmol)超声分散于50mL乙二醇中得到分散液A;称取对比例2制备的1.28g Bi2S3(2.5mmol)超声分散于20mL水中得到分散液B;将分散液B缓慢滴加至分散液A中,搅拌12h后洗涤干燥,所得材料记为BiOCl@Bi2S3-5。Weigh 1.3g BiOCl (5mmol) prepared in Comparative Example 1 and ultrasonically disperse it in 50mL of ethylene glycol to obtain dispersion A; Weigh 1.28g Bi 2 S3 (2.5mmol) prepared in Comparative Example 2 and ultrasonically disperse it in 20mL of water to obtain dispersion Liquid B; the dispersion liquid B was slowly added dropwise to the dispersion liquid A, stirred for 12 h, washed and dried, and the obtained material was denoted as BiOCl@Bi 2 S 3 -5.

抗生素降解:Antibiotic degradation:

室温下,分别将40mg实施例1-4和对比例1-3制备的材料加入到40mL含有一定浓度抗生素的水溶液中避光超声分散15min,暗反应30min,打开300W氙灯光源,反应一定时间后过滤除去催化剂,检测残留浓度,计算降解率如表1所示:At room temperature, 40 mg of the materials prepared in Examples 1-4 and Comparative Examples 1-3 were added to 40 mL of an aqueous solution containing a certain concentration of antibiotics for 15 minutes in the dark, and the reaction was dark for 30 minutes. The 300W xenon light source was turned on, and the reaction was filtered after a certain period of time. Remove the catalyst, detect the residual concentration, and calculate the degradation rate as shown in Table 1:

表1抗生素降解率数据表Table 1 Antibiotic degradation rate data table

实施例1Example 1 实施例2Example 2 实施例3Example 3 实施例4Example 4 对比例1Comparative Example 1 对比例2Comparative Example 2 对比例3Comparative Example 3 抗生素antibiotic 环丙沙星Ciprofloxacin 土霉素oxytetracycline 氧氟沙星Ofloxacin 诺氟沙星norfloxacin 诺氟沙星norfloxacin 诺氟沙星norfloxacin 诺氟沙星norfloxacin 降解时间(h)Degradation time (h) 1212 7.57.5 4.54.5 11 11 11 11 初始浓度(mg/L)Initial concentration (mg/L) 100100 6060 4545 1010 1010 1010 1010 残留浓度(mg/L)Residual concentration (mg/L) 3.53.5 4.14.1 2.82.8 0.120.12 5.85.8 6.96.9 3.23.2 降解率(%)Degradation rate(%) 96.596.5 93.293.2 93.893.8 98.898.8 4242 3131 6868

表2实施例1的BiOCl@Bi2S3-1催化初始浓度为100mg/L环丙沙星降解循环使用性能Table 2 The BiOCl@Bi 2 S 3 -1 catalytic initial concentration of Example 1 is 100 mg/L ciprofloxacin degradation and recycling performance

循环1次1 cycle 循环2次cycle 2 times 循环3次cycle 3 times 循环4次cycle 4 times 循环5次cycle 5 times 降解率(%)Degradation rate(%) 96.596.5 96.396.3 96.096.0 96.096.0 95.895.8

注:单次使用完成后,经过滤、洗涤、干燥重复使用。Note: After a single use, it can be reused after filtering, washing and drying.

VOCs降解:Degradation of VOCs:

室温下,分别将100mg实施例1-4和对比例1-3制备的材料加入到250mL一定浓度的VOCs气体中,打开300W氙灯光源,反应一定时间后,用气体取样器取样检测残留浓度,计算吸附率如表3所示:At room temperature, 100 mg of the materials prepared in Example 1-4 and Comparative Example 1-3 were added to 250 mL of VOCs gas of a certain concentration, and the 300W xenon light source was turned on. After a certain time of reaction, a gas sampler was used to sample and detect the residual concentration, and calculate the residual concentration. The adsorption rate is shown in Table 3:

表3 VOCs降解率数据表Table 3 VOCs degradation rate data table

Figure BDA0002918413030000051
Figure BDA0002918413030000051

Figure BDA0002918413030000061
Figure BDA0002918413030000061

表4实施例4的BiOCl@Bi2S3-4光催化初始浓度为1mg/L甲醛气体降解循环使用性能Table 4 The photocatalytic initial concentration of BiOCl@Bi 2 S 3 -4 in Example 4 is 1 mg/L formaldehyde gas degradation and recycling performance

循环1次1 cycle 循环2次cycle 2 times 循环3次cycle 3 times 循环4次cycle 4 times 循环5次cycle 5 times 降解率(%)Degradation rate(%) 99.299.2 99.199.1 99.199.1 99.099.0 98.798.7

注:单次使用完成后,直接重复使用。Note: After a single use is completed, it can be reused directly.

Claims (10)

1.一种BiOCl@Bi2S3复合材料的原位合成方法,其特征在于,包括如下步骤:1. an in-situ synthesis method of BiOCl@Bi 2 S 3 composite material, is characterized in that, comprises the steps: (1)将铋源溶于醇溶液,得溶液A;(1) bismuth source is dissolved in alcohol solution to obtain solution A; (2)将维生素B1盐酸盐溶于水中得溶液B,随后在搅拌下将溶液B加入至溶液A中,得到混合液C;(2) dissolving vitamin B 1 hydrochloride in water to obtain solution B, then adding solution B to solution A under stirring to obtain mixed solution C; (3)将混合液C进行水热处理,经固液分离、洗涤、干燥即得所述BiOCl@Bi2S3复合材料。(3) The mixed solution C is subjected to hydrothermal treatment, and the BiOCl@Bi 2 S 3 composite material is obtained through solid-liquid separation, washing and drying. 2.根据权利要求1所述的原位合成方法,其特征在于:步骤(1)中,所述铋源选自五水硝酸铋、氯化铋、柠檬酸铋中的一种或几种。2. in-situ synthesis method according to claim 1, is characterized in that: in step (1), described bismuth source is selected from one or more in bismuth nitrate pentahydrate, bismuth chloride, bismuth citrate. 3.根据权利要求1所述的原位合成方法,其特征在于:步骤(1)中,所述醇选自甲醇、乙醇、异丙醇、乙二醇、丙三醇中的一种或几种。3. in-situ synthesis method according to claim 1, is characterized in that: in step (1), described alcohol is selected from one or more in methanol, ethanol, isopropanol, ethylene glycol, glycerol kind. 4.根据权利要求1所述的原位合成方法,其特征在于:步骤(1)中,所述溶液A中,铋源的浓度为0.05~0.2mol/L。4. The in-situ synthesis method according to claim 1, characterized in that: in step (1), in the solution A, the concentration of the bismuth source is 0.05-0.2 mol/L. 5.根据权利要求1所述的原位合成方法,其特征在于:步骤(2)中,所述溶液B中,维生素B1盐酸盐的浓度为0.1~0.5mol/L。The in-situ synthesis method according to claim 1, characterized in that: in step (2), in the solution B, the concentration of vitamin B 1 hydrochloride is 0.1-0.5 mol/L. 6.根据权利要求1所述的一种BiOCl@Bi2S3复合材料的原位合成方法,其特征在于:步骤(2)中,所述铋源和维生素B1盐酸盐的摩尔比为1~5:1,。6. the in-situ synthesis method of a kind of BiOCl@Bi 2 S 3 composite material according to claim 1 , is characterized in that: in step (2), the mol ratio of described bismuth source and vitamin B hydrochloride is 1 to 5:1,. 7.根据权利要求1所述的原位合成方法,其特征在于:步骤(3)中,水热处理的温度为80~160℃,时间为6~24h。7 . The in-situ synthesis method according to claim 1 , wherein in the step (3), the temperature of the hydrothermal treatment is 80-160° C., and the time is 6-24 h. 8 . 8.权利要求1-7任一项所述的原位合成方法合成的BiOCl@Bi2S3复合材料的应用,其特征在于:将其作为可见光下抗生素或VOCs降解的光催化剂;8. the application of the BiOCl@Bi 2 S 3 composite material synthesized by the in-situ synthesis method described in any one of claims 1-7, is characterized in that: it is used as the photocatalyst that antibiotics or VOCs degrade under visible light; 具体步骤为:室温下,将BiOCl@Bi2S3复合材料加入到抗生素浓度为15~150mg/L的水中或VOCs浓度为0.2~2mg/L的气体中,反应0.1~12h即可。The specific steps are as follows: at room temperature, the BiOCl@Bi 2 S 3 composite material is added to water with an antibiotic concentration of 15-150 mg/L or gas with a VOCs concentration of 0.2-2 mg/L, and the reaction is sufficient for 0.1-12 h. 9.根据权利要求8所述的BiOCl@Bi2S3复合材料的应用,其特征在于:所述抗生素选自环丙沙星、诺氟沙星、氧氟沙星、四环素、磺胺甲恶唑、磺胺二甲基嘧啶和土霉素中的一种或多种,所述BiOCl@Bi2S3复合材料与抗生素的质量比为1:0.01~0.1。9. the application of BiOCl@Bi 2 S 3 composite material according to claim 8, is characterized in that: described antibiotic is selected from ciprofloxacin, norfloxacin, ofloxacin, tetracycline, sulfamethoxazole , one or more of sulfamethazine and oxytetracycline, and the mass ratio of the BiOCl@Bi 2 S 3 composite material to the antibiotic is 1:0.01-0.1. 10.根据权利要求8所述的BiOCl@Bi2S3复合材料的应用,其特征在于:10. the application of BiOCl@Bi 2 S 3 composite material according to claim 8, is characterized in that: 所述VOCs选自甲醛、甲苯、苯和二甲苯中的一种或多种,所述BiOCl@Bi2S3复合材料与VOCs的质量比为1:0.005~0.05。The VOCs are selected from one or more of formaldehyde, toluene, benzene and xylene, and the mass ratio of the BiOCl@Bi 2 S 3 composite material to the VOCs is 1:0.005-0.05.
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