CN106955718A - A kind of ZnS/Bi2O3Hetero-junctions molecular engram photocatalysis membrana and preparation method and purposes - Google Patents
A kind of ZnS/Bi2O3Hetero-junctions molecular engram photocatalysis membrana and preparation method and purposes Download PDFInfo
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Abstract
本发明提供了一种ZnS/Bi2O3异质结分子印迹光催化膜及制备方法和用途,制备方法如下:步骤1、制备Bi2O3光催化剂;步骤2、制备ZnS/Bi2O3异质结光催化剂;步骤3、制备ZnS/Bi2O3异质结分子印迹光催化膜。本发明制备选择性降解罗丹明B的分子印迹催化膜的光催化降解过程可以有效的实现对目标污染物选择性识别、吸附并催化降解的目的,后处理简单方便,提高了对目标物质的有效降解的效率,具有较强的选择性处理染料废水的优点。
The invention provides a ZnS/Bi 2 O 3 heterojunction molecularly imprinted photocatalyst film and its preparation method and application. The preparation method is as follows: Step 1, prepare Bi 2 O 3 photocatalyst; Step 2, prepare ZnS/Bi 2 O 3 Heterojunction photocatalyst; step 3, preparing a ZnS/Bi 2 O 3 heterojunction molecularly imprinted photocatalytic film. The photocatalytic degradation process of the molecularly imprinted catalytic membrane for selective degradation of rhodamine B prepared by the present invention can effectively realize the purpose of selective identification, adsorption and catalytic degradation of target pollutants, and the post-treatment is simple and convenient, which improves the effective efficiency of target substances. The degradation efficiency has the advantages of strong selective treatment of dye wastewater.
Description
技术领域technical field
本发明涉及一种利用相转化技术制备异质结结构半导体且具有光催化作用的分子印迹催化膜的方法,具体为一种高效降解罗丹明B的ZnS/Bi2O3异质结分子印迹光催化膜的制备方法及用途,属于材料制备及环境污染治理的技术领域。The invention relates to a method for preparing a molecularly imprinted catalytic film with a heterojunction structure semiconductor and photocatalysis by using phase inversion technology, in particular to a ZnS/Bi 2 O 3 heterojunction molecularly imprinted photocatalyst for efficiently degrading rhodamine B. The preparation method and application of the catalytic membrane belong to the technical field of material preparation and environmental pollution control.
背景技术Background technique
罗丹明B是一种人工合成碱性荧光染料同时它也是一种常见的分析试剂,广泛应用于环保、矿业、钢铁、医药等领域,也可作实验室中细胞荧光染色剂。曾用作食品添加剂,但实验证明罗丹明B会致癌,现已不允许用作食品添加剂及食品染色。由于这类化合物被排泄至水环境中,成为一种危害环境及人类健康的潜在风险,引起了环境生态学的广泛关注,因此,建立和发展有效和经济适用处理手段来选择性移除环境中罗丹明B残留是极为迫切的。Rhodamine B is a synthetic basic fluorescent dye, and it is also a common analytical reagent, widely used in environmental protection, mining, steel, medicine and other fields, and can also be used as a fluorescent stain for cells in laboratories. It was once used as a food additive, but experiments have proved that rhodamine B can cause cancer, and it is now not allowed to be used as a food additive and food dye. Since these compounds are excreted into the water environment, they become a potential risk to the environment and human health, which has aroused widespread concern in environmental ecology. Therefore, it is necessary to establish and develop effective and economical treatment methods to selectively remove Rhodamine B residues are extremely urgent.
光催化技术是利用半导体或复合半导体在光照条件下被激发,产生具有氧化还原功能的电子空穴对,从而降解污染物的一种方法。现在已广泛应用于研究水环境中染料的残留。人们通过对光催化剂进行改性来提高其光催化性能,但是仍然不具有选择性,难以在多种污染物共存的复杂水体中把目标物去除。因此,我们提出利用分子印迹技术与光电催化技术结合,使其具有特异识别功能,优先选择去除目标污染物。Photocatalytic technology is a method that uses semiconductors or compound semiconductors to be excited under light conditions to generate electron-hole pairs with redox functions, thereby degrading pollutants. Now it has been widely used to study the residue of dyes in the water environment. People have improved the photocatalytic performance by modifying the photocatalyst, but it is still not selective, and it is difficult to remove the target substance in the complex water body where multiple pollutants coexist. Therefore, we propose to use molecular imprinting technology combined with photoelectrocatalytic technology to make it have specific recognition function and preferentially select and remove target pollutants.
分子印迹膜技术是一种对目标分子具有专一识别能力的新型选择性分离膜,可以在分离膜材料的制备过程中采用分子印迹聚合物的合成方法,也可以通过在分离膜生产过程中引入印迹分子。分子印迹膜技术耦合了分子印迹与膜技术的优点,可以将特定的目标分子从混合物和其结构类似物中有效分离。Molecularly imprinted membrane technology is a new type of selective separation membrane that has the ability to specifically recognize target molecules. The synthesis method of molecularly imprinted polymers can be used in the preparation of separation membrane materials, or it can be introduced in the production process of separation membranes. imprinted molecules. Molecularly imprinted membrane technology combines the advantages of molecular imprinting and membrane technology, and can effectively separate specific target molecules from mixtures and their structural analogs.
将分子印迹膜技术与光催化技术相结合,制备得到具有选择性降解目标物的分子印迹催化膜,该催化膜能首先吸附目标分子,并优先降解,降解后再次实现吸附降解的循环体系,进而达到协同及促进选择性光催化降解目标污染物的目的。因此在选择性移除环境中罗丹明B类染料残留方面具有广阔的应用前景。Combining molecularly imprinted membrane technology with photocatalytic technology, a molecularly imprinted catalytic membrane with selective degradation of target substances is prepared. The catalytic membrane can firstly adsorb target molecules and degrade them preferentially. After degradation, the cycle system of adsorption and degradation can be realized again, and then To achieve the purpose of synergizing and promoting selective photocatalytic degradation of target pollutants. Therefore, it has broad application prospects in the selective removal of rhodamine B dye residues in the environment.
发明内容Contents of the invention
本发明利用相转化技术为制备手段,制备出一种对目标污染物罗丹明B具有特定选择性的分子印迹催化膜复合光催化剂。其优点在于在体系中构建一个循环过程,实现了对目标物质先吸附再催化降解,然后再吸附降解的循环过程,进而有效的利用光源达到有效降解环境中罗丹明B染料废水的目的。The invention uses the phase inversion technology as a preparation means to prepare a molecularly imprinted catalytic membrane composite photocatalyst with specific selectivity to target pollutant rhodamine B. Its advantage lies in the construction of a cyclic process in the system, which realizes the cyclic process of adsorbing the target substance first, then catalytically degrading it, and then adsorbing and degrading it, and then effectively using the light source to effectively degrade the rhodamine B dye wastewater in the environment.
本发明的技术方案是:Technical scheme of the present invention is:
一种ZnS/Bi2O3异质结分子印迹光催化膜,所述分子印迹光催化膜是由硫化锌球体和凸起状的Bi2O3结晶复合而成的,所述Bi2O3结晶负载于所述硫化锌球体表面。A ZnS/Bi 2 O 3 heterojunction molecularly imprinted photocatalytic film, the molecularly imprinted photocatalytic film is composed of zinc sulfide spheres and raised Bi 2 O 3 crystals, the Bi 2 O 3 Crystals are supported on the surface of the zinc sulfide spheres.
一种ZnS/Bi2O3异质结分子印迹光催化膜的制备方法,步骤如下:A method for preparing a ZnS/Bi 2 O 3 heterojunction molecularly imprinted photocatalytic film, the steps are as follows:
步骤1、制备Bi2O3光催化剂:将五水硝酸铋溶于去离子水中,得到硝酸铋溶液;将氢氧化钠溶液加入硝酸铋溶液,调节pH,搅拌,于室温下反应,反应完全后将混合液离心分离,用去离子水和无水乙醇分别洗涤多次,干燥,得淡黄色粉末A;将淡黄色粉末A置于马弗炉中,于一定温度下煅烧一定时间,得到Bi2O3光催化剂,待用;Step 1. Prepare Bi2O3 photocatalyst: Dissolve bismuth nitrate pentahydrate in deionized water to obtain bismuth nitrate solution; add sodium hydroxide solution to bismuth nitrate solution, adjust pH, stir, and react at room temperature, after the reaction is complete Centrifuge the mixed solution, wash with deionized water and absolute ethanol several times, and dry to obtain a light yellow powder A; place the light yellow powder A in a muffle furnace and calcinate at a certain temperature for a certain period of time to obtain Bi 2 O photocatalyst, stand - by;
步骤2、制备ZnS/Bi2O3异质结光催化剂:取二水合醋酸锌与硫脲搅拌下溶于去离子水中,并加入Bi2O3光催化剂,得混合液B;将混合液B移入不锈钢高压水热釜中,进行溶剂热反应,冷却后得混合液C;将混合液C过滤,并洗涤固体产物,干燥后研磨,得ZnS/Bi2O3异质结光催化剂,储存于采样管中,备用;Step 2. Preparation of ZnS/Bi 2 O 3 heterojunction photocatalyst: take zinc acetate dihydrate and thiourea, dissolve them in deionized water under stirring, and add Bi 2 O 3 photocatalyst to obtain mixed solution B; mix mixed solution B Move it into a stainless steel high-pressure hydrothermal kettle, perform solvothermal reaction, and obtain a mixed solution C after cooling; filter the mixed solution C, wash the solid product, dry and grind to obtain a ZnS/Bi 2 O 3 heterojunction photocatalyst, which is stored in In the sampling tube, spare;
步骤3、制备ZnS/Bi2O3异质结分子印迹光催化膜:取ZnS/Bi2O3异质结光催化剂加入到二甲亚砜中,超声分散得到ZnS/Bi2O3异质结光催化剂分散液;向ZnS/Bi2O3异质结光催化剂分散液中加入醋酸纤维素、壳聚糖和罗丹明B,40±5℃下搅拌混匀,机械搅拌均匀,得到铸膜液;将铸膜液于40±5℃下保温静置,脱去搅拌产生的气泡,然后取一洁净的玻璃板,将铸膜液平铺于玻璃板上,用玻璃棒刮出一定厚度,放置一段时间后,缓慢将其浸入去离子水中浸泡一段时间后取出,得到共混膜;将共混膜从玻璃板上剥下,置于甲醇/醋酸混合提取液中,浸泡一段时间以去除模板分子,然后将膜室温储存于去离子水中,备用。Step 3. Preparation of ZnS/Bi 2 O 3 heterojunction molecularly imprinted photocatalytic membrane: take ZnS/Bi 2 O 3 heterojunction photocatalyst and add it to dimethyl sulfoxide, and ultrasonically disperse it to obtain ZnS/Bi 2 O 3 heterostructure Junction photocatalyst dispersion; add cellulose acetate, chitosan and rhodamine B to the ZnS/Bi 2 O 3 heterojunction photocatalyst dispersion, stir and mix at 40±5°C, and mechanically stir evenly to obtain a cast film liquid; keep the casting solution at 40±5°C and keep it warm, remove the bubbles generated by stirring, then take a clean glass plate, spread the casting solution on the glass plate, scrape out a certain thickness with a glass rod, After standing for a period of time, slowly immerse it in deionized water for a period of time and then take it out to obtain a blended film; peel off the blended film from the glass plate, place it in a methanol/acetic acid mixed extraction solution, and soak for a period of time to remove the template molecules, and then store the membrane in deionized water at room temperature until use.
步骤1中,硝酸铋溶液中,所使用的五水硝酸铋粉末与去离子水的质量比为9.7:100;所使用的氢氧化钠溶液的浓度为0.5mol/L,所述pH为8;所述煅烧温度为300℃~500℃;所述煅烧时间为2h~6h。In step 1, in the bismuth nitrate solution, the mass ratio of the bismuth nitrate pentahydrate powder used to deionized water is 9.7:100; the concentration of the sodium hydroxide solution used is 0.5mol/L, and the pH is 8; The calcination temperature is 300°C-500°C; the calcination time is 2h-6h.
步骤2中,制混合液B时,所使用的二水合醋酸锌、硫脲、Bi2O3光催化剂和去离子水质量比为1.1:1.9:0.1:35;所述溶剂热反应的温度为170℃~210℃,时间为5h~24h;所述干燥的温度为60℃~80℃,干燥时间为12h~24h。In step 2, when making mixed solution B, used zinc acetate dihydrate, thiourea, Bi 2 O The photocatalyst and deionized water mass ratio are 1.1:1.9:0.1:35; The temperature of described solvothermal reaction is 170°C-210°C, the time is 5h-24h; the drying temperature is 60°C-80°C, and the drying time is 12h-24h.
步骤3中,制备ZnS/Bi2O3异质结光催化剂分散液时,所使用的ZnS/Bi2O3异质结催化剂与二甲亚砜的质量比为0.1~0.4:16.74~17.04;所述超声分散的时间为1~2h;所述铸膜液中,所述醋酸纤维素的质量分数为铸膜液的13%,壳聚糖的质量分数为铸膜液的1.0%,罗丹明B的质量分数为铸膜液的0.3%,所述机械搅拌的时间为4h;所述的保温静置时间为12~24h,共混膜的厚度为1.0mm;所述的放置的时间至少为30s,在去离子水中浸泡的时间至少为10min;所述甲醇/醋酸混合提取液中,甲醇、醋酸的体积比为9:1。In step 3, when preparing the ZnS/Bi 2 O 3 heterojunction photocatalyst dispersion, the mass ratio of the ZnS/Bi 2 O 3 heterojunction catalyst to dimethyl sulfoxide used is 0.1-0.4:16.74-17.04; The time for the ultrasonic dispersion is 1 to 2 hours; in the casting solution, the mass fraction of cellulose acetate is 13% of the casting solution, the mass fraction of chitosan is 1.0% of the casting solution, rhodamine The mass fraction of B is 0.3% of the casting liquid, the time of the mechanical stirring is 4h; the time of the heat preservation and standing is 12~24h, and the thickness of the blend film is 1.0mm; the time of the standing is at least 30s, soaking time in deionized water is at least 10min; in the methanol/acetic acid mixed extract, the volume ratio of methanol to acetic acid is 9:1.
所制备的ZnS/Bi2O3异质结分子印迹光催化膜用作光催化剂降解罗丹明B。The prepared ZnS/Bi 2 O 3 heterojunction molecularly imprinted photocatalytic film was used as a photocatalyst to degrade rhodamine B.
上述的技术方案中所述的二甲亚砜,其作用为溶剂,溶解醋酸纤维素和罗丹明B,以制备铸膜液。The dimethyl sulfoxide described in the above technical scheme acts as a solvent to dissolve cellulose acetate and rhodamine B to prepare a casting solution.
上述的技术方案中所述的醋酸纤维素,其作用为基质。The cellulose acetate described in the above-mentioned technical scheme acts as a matrix.
上述的技术方案中所述的壳聚糖,其作用为功能聚合物。The chitosan described in the above-mentioned technical scheme acts as a functional polymer.
上述的技术方案中所述的去离子水,其作用为非溶剂。The deionized water described in the above-mentioned technical scheme acts as a non-solvent.
上述的技术方案中所述的甲醇/醋酸混合提取液,其作用为阻断模板分子和功能聚合物间的氢键作用,从而洗脱模板分子。The methanol/acetic acid mixed extract solution described in the above technical solution functions to block the hydrogen bond between the template molecule and the functional polymer, thereby eluting the template molecule.
利用本发明采用分子印迹膜技术制备出的对罗丹明B具有选择性的分子印迹催化膜,对模板分子罗丹明B具有较高的选择性降解效果。The molecularly imprinted catalytic membrane with selectivity to rhodamine B prepared by using the molecularly imprinted membrane technology of the present invention has a relatively high selective degradation effect on the template molecule rhodamine B.
对应的非印迹共混膜(NIM)的制备方法与上述相同,但不加模板分子罗丹明B。The preparation method of the corresponding non-imprinted blend membrane (NIM) was the same as above, but no template molecule rhodamine B was added.
光催化活性评价:在DW-01型光化学反应仪中进行,可见光灯照射,将100mL一定浓度的罗丹明B模拟废水加入反应器中并测定其初始值,然后加入一定量的印迹膜及非印迹膜光催化剂,开启曝气装置通入空气,可以提供光催化过程中的氧气,光照过程中每间隔30min取样分析,离心分离后取上层清液在紫外-可见分光光度计λmax=554nm处测定吸光度,并通过公式:DC=[(A0-Ai)/A0]×100%算出降解率,其中A0为达到吸附平衡时罗丹明B溶液的吸光度,Ai为定时取样测定的罗丹明B溶液的吸光度。Evaluation of photocatalytic activity: carried out in DW-01 photochemical reaction apparatus, irradiated by visible light lamps, adding 100mL of rhodamine B simulated wastewater with a certain concentration into the reactor and measuring its initial value, and then adding a certain amount of imprinted membrane and non-imprinted membrane Membrane photocatalyst, open the aeration device and let in the air, which can provide oxygen in the photocatalytic process. During the photocatalytic process, samples are taken and analyzed at intervals of 30 minutes. After centrifugation, the supernatant is taken and measured at the UV-visible spectrophotometer at λ max = 554nm Absorbance, and calculate the degradation rate by the formula: DC=[(A 0 -A i )/A 0 ]×100%, where A 0 is the absorbance of rhodamine B solution when adsorption equilibrium is reached, and A i is the rhodamine measured by regular sampling The absorbance of the bright B solution.
本发明的技术优点:Technical advantage of the present invention:
首先,ZnS和Bi2O3都属于光催化剂,但是ZnS的禁带较宽,只在紫外光条件下有催化作用,而Bi2O3禁带较窄,能够被可见光激发,选择将这两种半导体结合形成异质结结构,能够使产生的光生电子从一种半导体注入另一种半导体,从而有效的阻止电子空穴的复合,这样就能提高光催化效率,提高对目标物质的降解率。其次,该技术采用水热合成法,步骤较为简单。最后,选择性降解罗丹明B的分子印迹催化膜的光催化降解过程可以有效的实现对目标污染物选择性识别、吸附并催化降解的目的,后处理简单方便,提高了对目标物质的有效降解的效率,具有较强的选择性处理染料废水的优点。First of all, both ZnS and Bi 2 O 3 belong to photocatalysts, but ZnS has a wide band gap and can only catalyze under ultraviolet light conditions, while Bi 2 O 3 has a narrow band gap and can be excited by visible light. Two kinds of semiconductors are combined to form a heterojunction structure, which can make the photogenerated electrons injected from one semiconductor into another semiconductor, thereby effectively preventing the recombination of electrons and holes, so as to improve the photocatalytic efficiency and the degradation rate of target substances . Secondly, the technology adopts the hydrothermal synthesis method, and the steps are relatively simple. Finally, the photocatalytic degradation process of the molecularly imprinted catalytic membrane that selectively degrades rhodamine B can effectively achieve the purpose of selective recognition, adsorption and catalytic degradation of target pollutants, and the post-treatment is simple and convenient, which improves the effective degradation of target substances The efficiency has the advantages of strong selective treatment of dye wastewater.
附图说明Description of drawings
图1为ZnS、Bi2O3、ZnS/Bi2O3的扫描电镜图,其中,图a为ZnS的扫描电镜图,图b为Bi2O3的扫描电镜图,图c为ZnS/Bi2O3的扫描电镜图;Figure 1 is the scanning electron micrograph of ZnS, Bi 2 O 3 , ZnS/Bi 2 O 3 , wherein, picture a is the scanning electron micrograph of ZnS, picture b is the scanning electron micrograph of Bi 2 O 3 , and picture c is the scanning electron micrograph of ZnS/Bi SEM image of 2 O 3 ;
图2为ZnS、Bi2O3、ZnS/Bi2O3的XRD谱图。Fig. 2 is the XRD spectrum of ZnS, Bi 2 O 3 , ZnS/Bi 2 O 3 .
具体实施方式detailed description
下面结合具体实施实例对本发明做进一步说明。The present invention will be further described below in conjunction with specific implementation examples.
本发明以铸膜液总质量为20g为例。In the present invention, the total mass of the casting solution is 20g as an example.
实施例1:Example 1:
(1)ZnS/Bi2O3异质结催化剂的制备(1) Preparation of ZnS/Bi 2 O 3 heterojunction catalyst
首先,将9.7g五水硝酸铋溶于100mL去离子水中,得到硝酸铋溶液,然后取500mL0.5mol·L-1氢氧化钠溶液逐滴加入硝酸铋溶液,搅拌,于室温下反应,得白色或淡黄色沉淀。离心分离,随后用去离子水和无水乙醇分别洗3次,离心分离后在60℃下干燥12h,将上述粉末放入马弗炉中于400℃下煅烧2h,得到Bi2O3催化剂,待用。取2.2g二水合醋酸锌和3.8g硫脲溶于70mL去离子水中,随后取0.2g Bi2O3光催化剂分散于上述溶液中,静置0.5h后,将上述溶液转移至不锈钢高压釜中,在170℃下加热5h,待冷却至室温后,随后用布氏漏斗真空抽滤并用去离子水和无水乙醇分别洗3次,在60℃~80℃下真空干燥12h~24h,最终得到ZnS/Bi2O3异质结催化剂。First, dissolve 9.7 g of bismuth nitrate pentahydrate in 100 mL of deionized water to obtain a bismuth nitrate solution, then take 500 mL of 0.5 mol L -1 sodium hydroxide solution and add it dropwise to the bismuth nitrate solution, stir, and react at room temperature to obtain a white Or pale yellow precipitate. Centrifuged, then washed three times with deionized water and absolute ethanol, dried at 60°C for 12 hours after centrifugal separation, put the above powder into a muffle furnace and calcined at 400°C for 2 hours to obtain a Bi2O3 catalyst, stand-by. Dissolve 2.2g of zinc acetate dihydrate and 3.8g of thiourea in 70mL of deionized water, then take 0.2g of Bi2O3 photocatalyst and disperse in the above solution, after standing for 0.5h, transfer the above solution to a stainless steel autoclave , heated at 170°C for 5h, cooled to room temperature, then vacuum-filtered with a Buchner funnel and washed three times with deionized water and absolute ethanol respectively, and vacuum-dried at 60°C-80°C for 12h-24h, and finally obtained ZnS/Bi 2 O 3 heterojunction catalyst.
(2)分子印迹催化膜的制备(2) Preparation of molecularly imprinted catalytic membrane
首先,取0.1gZnS/Bi2O3异质结催化剂加入17.04g二甲亚砜(DMSO)中,超声分散1~2h得到ZnS/Bi2O3异质结催化剂分散液,然后加入0.06g模板分子(罗丹明B)、2.6g膜基质(醋酸纤维素)和0.2g功能聚合物(壳聚糖),在40±5℃条件下机械搅拌4h至溶解均匀得到铸膜液,于40±5℃下保温静置12~24h,脱去搅拌产生的气泡,然后取一洁净的玻璃板,将铸膜液平铺于玻璃板上,用玻璃棒刮出1.0mm厚度的膜,30s后缓慢将其浸入去离子水中,浸泡30min后取出,即得分子印迹催化膜储存于去离子水中。非印迹膜的制备方法与上述相同,但不加模板分子罗丹明B。最后采用体积比为9:1的甲醇/醋酸混合溶液为提取液,以脱除模板分子罗丹明B,再用水洗涤数次至中性,将制得的分子印迹催化膜储存于去离子水中,作为对比,以同样的方法和步骤合成了空白非印迹催化膜,除了在聚合过程中不加模板分子罗丹明B。First, take 0.1g of ZnS/Bi 2 O 3 heterojunction catalyst and add it into 17.04g of dimethyl sulfoxide (DMSO), ultrasonically disperse for 1~2h to obtain ZnS/Bi 2 O 3 heterojunction catalyst dispersion, then add 0.06g of template Molecule (rhodamine B), 2.6g membrane matrix (cellulose acetate) and 0.2g functional polymer (chitosan), mechanically stirred at 40±5°C for 4h until dissolved to obtain a casting solution, at 40±5°C Keep it warm at ℃ for 12-24 hours, remove the bubbles generated by stirring, then take a clean glass plate, spread the casting solution on the glass plate, scrape out a film with a thickness of 1.0mm with a glass rod, and slowly remove it after 30s Immerse it in deionized water, take it out after soaking for 30 minutes, and store the molecularly imprinted catalytic membrane in deionized water. The non-imprinted membrane was prepared in the same way as above, but without adding the template molecule rhodamine B. Finally, the mixed solution of methanol/acetic acid with a volume ratio of 9:1 was used as the extraction solution to remove the template molecule rhodamine B, and then washed with water several times to neutrality, and the prepared molecularly imprinted catalytic membrane was stored in deionized water. As a comparison, a blank non-imprinted catalytic membrane was synthesized by the same method and steps, except that no template molecule rhodamine B was added during the polymerization process.
(3)分子印迹催化膜的光催化活性实验(3) Photocatalytic activity experiment of molecularly imprinted catalytic membrane
取10g步骤(2)中制备的样品在光化学反应仪中进行光催化降解试验,加入100mL,20mg·L-1的罗丹明B溶液中,磁力搅拌暗吸附1h,打开循环水源,光源,进行光催化降解实验,每30min吸取4-6ml反应器中的光催化降解液,用紫外-可见分光光度计测其在554nm处的吸光度,并通过公式:DC%=[(A0-Ai)/A0]×100%算出降解率,其中A0为达到吸附平衡时罗丹明B溶液的吸光度,Ai为定时取样测定的罗丹明B溶液的吸光度。降解率表示(2)中制备的催化剂的光催化活性。Take 10 g of the sample prepared in step (2) and carry out the photocatalytic degradation test in a photochemical reaction apparatus, add 100 mL, 20 mg L -1 rhodamine B solution, magnetically stir for 1 h, turn on the circulating water source, light source, and carry out photocatalytic degradation test. For the catalytic degradation experiment, absorb the photocatalytic degradation solution in 4-6ml reactor every 30min, measure its absorbance at 554nm with a UV-visible spectrophotometer, and use the formula: DC%=[(A 0 -A i )/ A 0 ] × 100% to calculate the degradation rate, wherein A 0 is the absorbance of the rhodamine B solution when the adsorption equilibrium is reached, and A i is the absorbance of the rhodamine B solution measured by regular sampling. The degradation rate indicates the photocatalytic activity of the catalyst prepared in (2).
图1为ZnS、Bi2O3、ZnS/Bi2O3的扫描电镜图。从图a可看出,ZnS为球状,图b为Bi2O3的结晶状态,图c中可以看出,ZnS球体周围有凸起状的Bi2O3结晶。Fig. 1 is a scanning electron microscope image of ZnS, Bi 2 O 3 , ZnS/Bi 2 O 3 . It can be seen from Figure a that ZnS is spherical, Figure b is the crystallization state of Bi 2 O 3 , and it can be seen from Figure c that there are convex Bi 2 O 3 crystals around the ZnS sphere.
图2为ZnS、Bi2O3和ZnS/Bi2O3复合材料的XRD谱图。氧化铋在27°和34°处有尖锐的特征峰,硫化锌在28.9°,48.8°和57.2°处存在明显衍射峰,及对应硫化锌的(111),(220),(311)晶面,同时复合物XRD图中看出,明显存在硫化锌的(220),(311)晶面的衍射峰,而(111)晶面衍射峰与氧化铋的衍射峰重合。Figure 2 is the XRD spectra of ZnS, Bi 2 O 3 and ZnS/Bi 2 O 3 composite materials. Bismuth oxide has sharp characteristic peaks at 27° and 34°, and zinc sulfide has obvious diffraction peaks at 28.9°, 48.8° and 57.2°, corresponding to (111), (220), (311) crystal planes of zinc sulfide , At the same time, it can be seen from the composite XRD figure that the diffraction peaks of (220) and (311) crystal planes of zinc sulfide obviously exist, and the diffraction peaks of (111) crystal plane coincide with the diffraction peaks of bismuth oxide.
实施例2:Example 2:
保证其他条件不变的情况下,建立对比试验如下:(1)制Bi2O3光催化剂时,煅烧温度取300℃,煅烧时间4h,水热法合成ZnS/Bi2O3异质结光催化剂时,反应釜反应温度取210℃,反应时间5h,反应结束后,用相同方法洗涤并干燥,研磨得到粉体催化剂,待用。(2)制Bi2O3光催化剂时,煅烧温度取500℃,煅烧时间6h,水热法合成ZnS/Bi2O3异质结光催化剂时,反应釜反应温度取170℃,反应时间24h,反应结束后,用相同方法洗涤并干燥,研磨得到粉体催化剂,待用。得到的不同条件下制得的催化剂,用于降解罗丹明B,观察并计算降解效率。Under the condition that other conditions remain unchanged, the comparative experiment is established as follows: (1) When preparing Bi 2 O 3 photocatalyst, the calcination temperature is 300°C, the calcination time is 4h, and the ZnS/Bi 2 O 3 heterojunction photocatalyst is synthesized by hydrothermal method. For the catalyst, the reaction temperature of the reactor is 210°C, and the reaction time is 5 hours. After the reaction, wash and dry in the same way, and grind to obtain a powder catalyst for use. (2) When preparing Bi 2 O 3 photocatalyst, the calcination temperature is 500°C, and the calcination time is 6h; when the ZnS/Bi 2 O 3 heterojunction photocatalyst is synthesized by hydrothermal method, the reaction temperature of the reactor is 170°C, and the reaction time is 24h , after the reaction is over, wash and dry in the same way, and grind to obtain a powder catalyst, which is ready for use. The obtained catalysts prepared under different conditions were used to degrade rhodamine B, and the degradation efficiency was observed and calculated.
实施例3:Example 3:
(1)通过改变ZnS/Bi2O3异质结光催化剂的用量(0.2g,0.3g,0.4g)来考查催化剂投加量对光催化降解的影响,在改变ZnS/Bi2O3异质结光催化剂的用量的同时,改变二甲亚砜的用量(16.94g,16.84g,16.74g),保证ZnS/Bi2O3异质结光催化剂、二甲亚砜的总质量分数为85.7%,结果表明在催化剂用量为0.4g时,其对罗丹明B的降解效率最高,可以达到90%以上。所以实验中所选择的催化剂用量为0.4g。(1) By changing the amount of ZnS/Bi 2 O 3 heterojunction photocatalyst (0.2g, 0.3g, 0.4g) to examine the effect of catalyst dosage on photocatalytic degradation, when changing ZnS/Bi 2 O 3 While changing the amount of photocatalyst, change the amount of dimethyl sulfoxide (16.94g, 16.84g, 16.74g) to ensure that the total mass fraction of ZnS/Bi 2 O 3 heterojunction photocatalyst and dimethyl sulfoxide is 85.7 %, the results show that when the catalyst dosage is 0.4g, its degradation efficiency to Rhodamine B is the highest, which can reach more than 90%. Therefore, the amount of catalyst selected in the experiment was 0.4 g.
(2)用0.4g光催化剂所制备的分子印迹催化膜在可见光下催化降解不同浓度(10,20,30,40,50mg·L-1)的罗丹明B溶液,考查在不同浓度时分子印迹光催化膜对罗丹明B的降解动力学,通过计算并且拟合动力学方程可知,分子印迹光催化剂降解罗丹明B的过程符合准一级动力学模型,当罗丹明B起始浓度为20mg·L-1时,分子印迹光催化膜对罗丹明B的平均降解速率为0.048min-1。(2) Molecularly imprinted catalytic membrane prepared with 0.4g photocatalyst degrades rhodamine B solutions with different concentrations (10, 20, 30, 40, 50 mg·L -1 ) under visible light, and examines the molecular imprinted membrane at different concentrations The degradation kinetics of rhodamine B by the photocatalytic film is calculated and fitted to the kinetic equation. It can be known that the process of molecularly imprinted photocatalyst degradation of rhodamine B conforms to the pseudo-first-order kinetic model. When the initial concentration of rhodamine B is 20mg· At L -1 , the average degradation rate of rhodamine B by the molecularly imprinted photocatalytic membrane was 0.048min -1 .
实施例4:Example 4:
分别用例1中的(2)中制备的光催化膜降解相同浓度的罗丹明B和干扰物质(亚甲基蓝)的混合溶液,通过计算对不同物质的降解效率进而计算其对不同物质的选择性系数。The photocatalytic film prepared in (2) in Example 1 was used to degrade the mixed solution of rhodamine B and interfering substance (methylene blue) at the same concentration, and the selectivity coefficient for different substances was calculated by calculating the degradation efficiency of different substances.
其中C0,Ce分别为罗丹明B起始和降解后的浓度(mg·L-1);D为分配系数,DCIP,DM分别为罗丹明B和干扰物质的分配系数;α是选择性系数,αi,αn分别为印迹和空白聚合物光催化剂的选择性系数,αr是相对选择性系数。Among them, C 0 , C e are the initial and degraded concentrations of rhodamine B (mg·L -1 ); D is the partition coefficient, D CIP , and D M are the partition coefficients of rhodamine B and interfering substances; α is The selectivity coefficients, α i , α n are the selectivity coefficients of imprinted and blank polymer photocatalysts, respectively, and α r is the relative selectivity coefficient.
实验结果表明,分子印迹光催化膜对罗丹明B的降解效率明显高于其他对比的物质,选择性系数也都大于其他干扰物质,分子印迹光催化膜对罗丹明B和亚甲基蓝的相对选择性系数分别为3.28和1.57。说明用此方法合成的分子印迹催化膜对罗丹明B具有较好的选择性,从而实现了对目标物质罗丹明B选择性催化降解的目的。The experimental results show that the degradation efficiency of the molecularly imprinted photocatalytic membrane on rhodamine B is significantly higher than that of other contrasting substances, and the selectivity coefficients are also greater than other interfering substances. The relative selectivity coefficient of the molecularly imprinted photocatalytic membrane on rhodamine B and methylene blue 3.28 and 1.57, respectively. It shows that the molecularly imprinted catalytic membrane synthesized by this method has good selectivity to rhodamine B, thus realizing the purpose of selective catalytic degradation of target substance rhodamine B.
实施例5:Example 5:
(1)首先用例1中的(2)中制备的光催化剂单独吸附不同浓度的罗丹明B、亚甲基蓝,甲基橙的溶液。根据公式计算印迹催化膜对不同物种的吸附容量。Q=(C0-Ce)*V/m,其中Q是吸附剂的吸附容量(mg·g-1),C0,Ce分别为罗丹明B吸附前和吸附平衡后的浓度(mg·L-1),V是罗丹明B溶液的体积(L),m是吸附剂的质量(g)。实验结果显示,分子印迹光催化膜对模板分子罗丹明B的吸附容量普遍大于对其他物质的吸附容量,而非印迹催化膜对这几种物质的吸附容量相差不大。(1) First use the photocatalyst prepared in (2) in Example 1 to separately adsorb different concentrations of rhodamine B, methylene blue, and methyl orange solutions. The adsorption capacity of the imprinted catalytic membrane for different species was calculated according to the formula. Q=(C 0 -C e )*V/m, where Q is the adsorption capacity of the adsorbent (mg·g -1 ), C 0 , and C e are the concentration of rhodamine B before adsorption and after adsorption equilibrium (mg ·L −1 ), V is the volume (L) of the rhodamine B solution, and m is the mass (g) of the adsorbent. The experimental results show that the adsorption capacity of the molecularly imprinted photocatalytic membrane for the template molecule rhodamine B is generally greater than that of other substances, while the adsorption capacity of the non-imprinted catalytic membrane for these substances is not much different.
(2)分别用例1中的(2)中制备的光催化膜吸附相同浓度的罗丹明B、亚甲基蓝和甲基橙的混合溶液,经过相同的吸附时间,离心分离悬浮溶液,测定上清液的浓度,根据公式计算催化剂对不同物种的吸附容量,然后计算其对不同物质的吸附选择性。结果表明分子印迹光催化膜对罗丹明B的吸附容量明显高于其对亚甲基蓝和甲基橙的吸附容量,而非印迹催化膜对三者的吸附容量差别不大,说明在印迹过程中提高了印迹膜对罗丹明B的吸附容量。(2) The photocatalytic membrane prepared in (2) in Example 1 is used to adsorb the mixed solution of rhodamine B, methylene blue and methyl orange of the same concentration respectively, and through the same adsorption time, the suspended solution is centrifuged to measure the concentration of the supernatant. Concentration, according to the formula to calculate the adsorption capacity of the catalyst for different species, and then calculate its adsorption selectivity for different substances. The results showed that the adsorption capacity of molecularly imprinted photocatalytic membranes for rhodamine B was significantly higher than that of methylene blue and methyl orange, while the adsorption capacities of non-imprinted catalytic membranes were not much different, which indicated that the adsorption capacity of rhodamine B was increased during the imprinting process. Adsorption capacity of imprinted membranes for Rhodamine B.
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| CN109590026B (en) * | 2018-11-30 | 2021-09-24 | 河海大学 | A kind of composite photocatalytic material and its preparation method and application |
| CN109589992A (en) * | 2018-12-03 | 2019-04-09 | 江苏大学 | A kind of MoS2/Bi2O3The preparation method and applications of p-n heterojunction photochemical catalyst |
| CN109967095A (en) * | 2019-04-17 | 2019-07-05 | 南昌航空大学 | A kind of all-crystalline heterojunction photocatalytic material and its preparation method and application |
| CN109967095B (en) * | 2019-04-17 | 2021-05-25 | 南昌航空大学 | Full-crystal heterojunction photocatalytic material and preparation method and application thereof |
| CN110947401A (en) * | 2019-12-30 | 2020-04-03 | 四川大学 | A kind of Bi2WO6/ZnS heterojunction photocatalyst and preparation method thereof |
| CN114700087A (en) * | 2022-04-28 | 2022-07-05 | 广西大学 | Efficient visible light photocatalytic material and preparation method and application thereof |
| CN114700087B (en) * | 2022-04-28 | 2023-09-29 | 广西大学 | A high-efficiency visible light photocatalytic material and its preparation method and application |
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