CN102794186A - Oxyhalide photo-catalytic material and preparation method thereof - Google Patents
Oxyhalide photo-catalytic material and preparation method thereof Download PDFInfo
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Abstract
本发明涉及卤氧化物光催化材料及其制备方法,属于光催化材料领域。本发明利用固相或液相法制备卤氧化物光催化材料,其特征在于其化学组成为BiOX,X=Cl,Br,I,[Bi2O2]与[X]结构层沿c轴方向交替相互堆积,形成层状晶体构型。制备所得的BiOX(X=Cl,Br,I)均具有优异的光催化性能,可降解有机染料,降解有机有害气体,杀菌和光解水产氢。负载Ag和Pt等电子亲和力强的纳米金属颗粒,可以大幅度提高材料的光催化性能。The invention relates to an oxyhalide photocatalytic material and a preparation method thereof, belonging to the field of photocatalytic materials. The present invention utilizes a solid-phase or liquid-phase method to prepare an oxyhalide photocatalytic material, which is characterized in that its chemical composition is BiOX, X=Cl, Br, I, [Bi 2 O 2 ] and the [X] structural layer along the c-axis direction Alternately stacked on each other to form a layered crystal configuration. The prepared BiOX (X=Cl, Br, I) all have excellent photocatalytic properties, can degrade organic dyes, degrade organic harmful gases, sterilize and produce hydrogen by photolyzing water. The photocatalytic performance of the material can be greatly improved by loading Ag and Pt and other nano-metal particles with strong electron affinity.
Description
技术领域 technical field
本发明涉及卤氧化物光催化材料及其制备方法,属于光催化材料领域,尤其属于染料降解、光解水产氢、有机有害气体降解、杀菌等领域。The invention relates to an oxyhalide photocatalytic material and a preparation method thereof, and belongs to the field of photocatalytic materials, in particular to the fields of dye degradation, hydrogen production by photolysis of water, degradation of organic harmful gases, sterilization and the like.
背景技术 Background technique
自1972年Fujishima和Honda发现在TiO2电极材料表面光响应产氢现象以来,光催化作为解决环境污染和能源危机一种潜在技术引起全世界的关注。在半导体光催化过程中,光照射激发价带中的电子跃迁至导带,即在导带上形成光生电子和价带上形成光生空穴;载流子迁移到粉末颗粒表面后,充分与周围的环境作用,发生复杂的氧化、还原反应。藉于此,利用电子的强还原特性和空穴的氧化作用,能够将水中的H+和OH-分别还原和氧化成H2和O2;另外,迁移到光催化剂表面的电子和空穴还能与环境中的O2、H+、OH-等作用形成·O2 -、·OH和HO2 -等活性强氧化剂,用于氧化降解和净化液相、气相中的有机污染物。Since Fujishima and Honda discovered the phenomenon of photoresponsive hydrogen production on the surface of TiO 2 electrode materials in 1972, photocatalysis has attracted worldwide attention as a potential technology to solve environmental pollution and energy crisis. In the process of semiconductor photocatalysis, light irradiation excites electrons in the valence band to transition to the conduction band, that is, photogenerated electrons are formed on the conduction band and photogenerated holes are formed on the valence band; Under the influence of the environment, complex oxidation and reduction reactions occur. In this way, the strong reduction characteristics of electrons and the oxidation of holes can be used to reduce and oxidize H + and OH - in water to H 2 and O 2 respectively; in addition, the electrons and holes that migrate to the surface of the photocatalyst It can react with O 2 , H + , OH - in the environment to form strong active oxidants such as ·O 2 - , ·OH and HO 2 - , which are used for oxidative degradation and purification of organic pollutants in liquid and gas phases.
除了潜在的光解水产氢能源用途外,光催化技术在实际解决环境污染问题中已崭露头角。目前,以成本低廉、具有高化学稳定性的TiO2为基材的光催化技术已经在防日晒化妆品、高级轿车金属色面漆和电子工业、复印机行业、高压绝缘材料、集成电路基板、荧光管以及其他更多的领域得到了应用。据介绍,这种光催化技术还可广泛应用于卫生陶瓷、玻璃制品、燃具、数字键盘以及空调、冰箱、洗衣机等家用电器,将给建筑材料、家用电器以及人们的日常生活带来巨大变革。有关专家称,这种技术如果大规模推广应用,将有望成为解决环境污染问题的高科技利器。In addition to the potential use of photolysis of water to produce hydrogen energy, photocatalysis technology has emerged in the actual solution to environmental pollution problems. At present, the photocatalytic technology based on TiO2 with low cost and high chemical stability has been used in anti-sun cosmetics, metallic paint for luxury cars and electronics industry, copier industry, high-voltage insulation materials, integrated circuit substrates, fluorescent Tubes and many other fields have been applied. According to reports, this photocatalytic technology can also be widely used in sanitary ceramics, glass products, gas appliances, digital keyboards, and household appliances such as air conditioners, refrigerators, washing machines, etc., which will bring about great changes in building materials, household appliances and people's daily life . According to relevant experts, if this technology is popularized and applied on a large scale, it is expected to become a high-tech weapon to solve the problem of environmental pollution.
目前国内外光催化剂的研究多数停留在TiO2及相关修饰,如材料的纳米化及高比表面化、掺杂、半导体复合、贵金属及氧化物负载等。尽管这些工作卓有成效,但其量子产率不高,而且难以用于光催化裂解水产氢之用途,因此,找寻新型高效光催化剂已成为当前此领域最重要的课题之一。根据已发现的光催化材料,其体系归类可分为氧化物、硫化物、氧硫化物、氮化物以及氧氮化物,其中氧化物往往有比较好的(光)化学稳定性;硫化物及氧硫化物虽然能够显示较理想的可见光响应特性,但作为光催化材料容易产生光化学腐蚀;氮化物及氧氮化物也具有较好的可见光吸收特性,其材料本身光催化效果不尽理想,但在负载电子亲和力强的贵金属或其氧化物后,光催化活性能够得以急剧提高,如负载Rh-Cr纳米复合氧化物的(GaN)x(ZnO)1-x固溶体粉末可见光响应光催化裂解水产氢速率可以达到mmol/h数量级,而未负载的粉末光催化活性极差。At present, most of the research on photocatalysts at home and abroad stays on TiO 2 and related modifications, such as nanometerization and high specific surface of materials, doping, semiconductor recombination, noble metal and oxide loading, etc. Although these works are very effective, their quantum yield is not high, and it is difficult to be used for hydrogen production by photocatalytic cracking of water. Therefore, finding new high-efficiency photocatalysts has become one of the most important issues in this field. According to the discovered photocatalytic materials, their systems can be classified into oxides, sulfides, oxysulfides, nitrides and oxynitrides, among which oxides often have better (photo) chemical stability; sulfides and Although oxysulfide can show relatively ideal visible light response characteristics, it is prone to photochemical corrosion as a photocatalytic material; nitride and oxynitride also have good visible light absorption characteristics, and the photocatalytic effect of the material itself is not ideal, but in After loading noble metals with strong electron affinity or their oxides, the photocatalytic activity can be greatly improved, such as (GaN) x (ZnO) 1-x solid solution powder loaded with Rh-Cr nanocomposite oxides in response to photocatalytic cracking of water hydrogen production rate under visible light It can reach the order of mmol/h, but the photocatalytic activity of unloaded powder is extremely poor.
寻找新型高效光催化剂一直是光催化技术领域一项长期而艰巨的任务,它是光催化技术能够得以大规模推广应用尤其在光解水制氢领域应用的核心所在。Finding new high-efficiency photocatalysts has always been a long-term and arduous task in the field of photocatalysis technology. It is the core of the large-scale application of photocatalysis technology, especially in the field of photolysis of water to produce hydrogen.
发明内容 Contents of the invention
本发明的目的在于提供一种新型的卤氧化物光催化材料及多种制备方法。The purpose of the present invention is to provide a novel oxyhalide photocatalytic material and various preparation methods.
在BiOX(X=Cl,Br,I)晶体结构中,[Bi2O2]与[X]结构层沿c轴方向交替相互堆积,形成这类独特的层状晶体构型。利用密度泛函(DFT)能带理论计算方法进行BiOX(X=Cl,Br,I)能带计算,结果显示,导带主要由Bi 6p轨道组成,价带主要由Cl 3p(或Br 4p,I5p)组成;BiOX(X=Cl,Br,I)半导体是一种间接跃迁材料,Bi6p在导带中较为弥散,有利于电子在材料内部的传输,提高电子导电性及相应的光生电子-空穴分离能力。紫外-可见光吸收光谱显示,BiOX(X=Cl,Br,I)材料吸收边分别对应为358,426,646nm左右,其光学禁带宽度相应在3.46,2.91,1.92eV左右。In the BiOX (X=Cl, Br, I) crystal structure, [Bi 2 O 2 ] and [X] structural layers are stacked alternately along the c-axis direction to form this unique layered crystal structure. Using the density functional (DFT) band theory calculation method to calculate the energy band of BiOX (X=Cl, Br, I), the results show that the conduction band is mainly composed of
我们采用多种固相或液相等多种方法来合成材料,并对材料进行光催化性能测试。We use a variety of methods such as solid phase or liquid to synthesize materials, and test the photocatalytic performance of materials.
一、材料制备1. Material preparation
方法一:method one:
将Bi2O3粉体溶解于浓卤酸(HCl、HBr、HI)中,用氨水调节至pH=2~5,经过多次过滤直至检测不到X-离子(用硝酸银溶液检验)后,沉淀物烘干即得成品光催化粉末。Dissolve Bi 2 O 3 powder in concentrated halogen acid (HCl, HBr, HI), adjust to pH=2~5 with ammonia water, and filter for many times until no X - ions can be detected (tested with silver nitrate solution) , and the precipitate is dried to obtain the finished photocatalytic powder.
负载的BiOX(X=Cl,Br,I)光催化材料的具体过程可为:取BiOX(X=Cl,Br,I)催化剂粉末置入含有去离子水的烧杯中,加入足量的甲醇空穴牺牲剂和0.05~5wt%的AgNO3或0.05~5wt%H2PtCl6·6H2O,强力搅拌的同时在汞灯下照射5~10h,经过多次过滤洗涤,干燥即得负载有纳米Ag或Pt颗粒的光催化材料。The specific process of the supported BiOX (X=Cl, Br, I) photocatalytic material can be: take the BiOX (X=Cl, Br, I) catalyst powder and place it in a beaker containing deionized water, add a sufficient amount of methanol to Hole sacrificial agent and 0.05-5wt% AgNO 3 or 0.05-5wt% H 2 PtCl 6 ·6H 2 O, irradiated under a mercury lamp for 5-10 hours while vigorously stirring, filtered and washed several times, and dried to obtain nano Photocatalytic materials of Ag or Pt particles.
所得的BiOX(X=Cl,Br,I)光催化粉体粒径为5~120nm,负载有0.05~5wt%的Ag或Pt。The obtained BiOX (X=Cl, Br, I) photocatalytic powder has a particle diameter of 5-120 nm, and is loaded with 0.05-5 wt % of Ag or Pt.
方法二:Method Two:
将按化学计量比的Bi2O3和BiX3(X=Cl,Br,I)粉体置于石英管中,抽真空后封装,在400-750℃加热2-24小时。冷却后开管研磨即得成品光催化粉末。The stoichiometric ratio of Bi 2 O 3 and BiX 3 (X=Cl, Br, I) powders is placed in a quartz tube, vacuumized and packaged, and heated at 400-750° C. for 2-24 hours. After cooling, open the tube and grind to get the finished photocatalytic powder.
方法三:Method three:
取去离子水于烧杯中,用相应卤酸调节溶液pH小于1,然后将溶液加热,在不断搅拌的同时,缓慢加入化学计量比的硝酸铋-卤酸溶液,同时缓慢加入浓度为5~20%NaOH溶液以中和水解产生的HNO3,维持pH值在2~5,整个过程持续约0.5~5h。其间温度恒定在50~90℃左右,继续搅拌10min以上,冷却、过滤、洗涤、烘干即得成品光催化粉末。Take deionized water in a beaker, use the corresponding halogen acid to adjust the pH of the solution to less than 1, then heat the solution, and while stirring continuously, slowly add the stoichiometric ratio of bismuth nitrate-halogen acid solution, and at the same time slowly add the concentration of 5 to 20 % NaOH solution to neutralize the HNO 3 produced by hydrolysis, and maintain the pH value at 2-5, and the whole process lasts for about 0.5-5 hours. During this period, the temperature is kept constant at about 50-90°C, and the stirring is continued for more than 10 minutes, and the finished photocatalytic powder is obtained by cooling, filtering, washing, and drying.
方法四:Method four:
加入化学计量比的卤酸、固体硝酸铋混合,然后加入占混合物重量0.5~5%无水硫酸钠和0.5~5%十二烷基苯磺酸钠溶液,再加入热水搅拌得到透明溶液,然后放入微波炉中微波辐照2~3分钟,取出急冷,过滤、洗涤、烘干即得成品光催化粉末。adding a stoichiometric ratio of halogen acid and solid bismuth nitrate to mix, then adding 0.5-5% anhydrous sodium sulfate and 0.5-5% sodium dodecylbenzenesulfonate solution based on the weight of the mixture, adding hot water and stirring to obtain a transparent solution, Then put it into a microwave oven and irradiate it with microwaves for 2 to 3 minutes, take it out for rapid cooling, filter, wash and dry to obtain the finished photocatalytic powder.
方法五:Method five:
取化学计量比硝酸铋-卤酸溶液,不断搅拌的同时加入过量比的碱金属卤化物(与卤酸对应),然后用稀氨水调节pH为2~5,搅拌,过滤、洗涤、烘干即得成品光催化粉末。Take the stoichiometric ratio bismuth nitrate-halogen acid solution, add an excess ratio of alkali metal halide (corresponding to the halogen acid) while stirring continuously, then adjust the pH to 2-5 with dilute ammonia water, stir, filter, wash, and dry. The finished photocatalytic powder is obtained.
方法六:Method six:
将硝酸铋溶解于足量冰醋酸中,搅拌的同时快速加入碳酸钠和碱金属卤化物的混合溶液,碳酸钠和碱金属卤化物的摩尔比为1∶(0.5~1.5),剧烈搅拌后,过滤、洗涤、烘干即得成品光催化粉末。Dissolve bismuth nitrate in sufficient amount of glacial acetic acid, quickly add the mixed solution of sodium carbonate and alkali metal halide while stirring, the molar ratio of sodium carbonate and alkali metal halide is 1: (0.5~1.5), after vigorous stirring, Filter, wash and dry to get the finished photocatalytic powder.
二、性能评价(光催化性能)2. Performance evaluation (photocatalytic performance)
选用P25-TiO2光催化剂定性评判BiOX(X=Cl,Br,I)的光催化活性,实验过程同BiOX(X=Cl,Br,I)。Select P25-TiO 2 photocatalyst to qualitatively evaluate the photocatalytic activity of BiOX (X=Cl, Br, I), and the experiment process is the same as that of BiOX (X=Cl, Br, I).
(1)染料降解和光解水产氢(1) Dye degradation and hydrogen production by photolysis of water
将本发明所得样品粉末在自制的反应器中进行光催化降解有机染料(甲基橙)以及光催化分解水产氢的研究。照射灯源为500W的高压汞光灯。催化实验时,染料的浓度为:10mg/L,粉末在染料溶液中或纯水中的量为:0.2g/100mL。The sample powder obtained in the present invention is used in a self-made reactor to carry out photocatalytic degradation of organic dyes (methyl orange) and photocatalytic decomposition of water to produce hydrogen. The light source is a 500W high-pressure mercury lamp. During the catalytic experiment, the concentration of the dye is: 10mg/L, and the amount of the powder in the dye solution or pure water is: 0.2g/100mL.
(2)有害气体降解(2) Harmful gas degradation
将本发明所得样品粉末在自制的反应器中进行光催化降解代表性有害气体甲醛的研究。光催化反应在自制的圆柱型不锈钢光催化反应器中进行,光源为8W紫外灯(PHILIPS公司)。光催化剂用水均匀地涂在一块70mm×70mm×2mm的正方形玻璃片上,烘干后将其悬挂在反应器中的紫外灯与轴流风扇之间。先将反应系统抽真空,反应器为密闭的容器。抽真空后,通入干燥空气,直至达到大气压。然后将一定量的固体多聚甲醛气化后,注入反应容器中。实验开始时关闭紫外光源,当系统内甲醛含量不再减少即已达吸附平衡时开启紫外灯,进行UV照射,每隔20min用气相色谱仪检测系统内甲醛气体浓度,按ΔC/C0计算光催化氧化分解甲醛的降解率。The sample powder obtained in the present invention is carried out in a self-made reactor for photocatalytic degradation of representative harmful gas formaldehyde. The photocatalytic reaction was carried out in a self-made cylindrical stainless steel photocatalytic reactor, and the light source was an 8W ultraviolet lamp (PHILIPS company). The photocatalyst is evenly coated with water on a square glass sheet of 70mm×70mm×2mm, and after drying, it is suspended between the ultraviolet lamp and the axial flow fan in the reactor. Vacuumize the reaction system first, and the reactor is a closed container. After vacuuming, dry air was introduced until atmospheric pressure was reached. Then a certain amount of solid paraformaldehyde is vaporized and injected into the reaction vessel. Turn off the UV light source at the beginning of the experiment, turn on the UV lamp when the formaldehyde content in the system no longer decreases and reaches the adsorption equilibrium, and perform UV irradiation. Use a gas chromatograph to detect the concentration of formaldehyde gas in the system every 20 minutes, and calculate the light according to ΔC/C 0 Degradation rate of catalytic oxidative decomposition of formaldehyde.
(3)杀菌测试(3) Sterilization test
选取大肠杆菌E.coli及金黄色葡萄球菌作为试验菌种。用牛肉膏蛋白胨培养基对细菌进行繁殖。采用血细胞计数板在显微镜下直接计数测定溶液中所含菌量来测定粉体的杀菌效率。Escherichia coli E.coli and Staphylococcus aureus were selected as the test strains. Bacteria were propagated with beef extract peptone medium. Use a hemocytometer to directly count and measure the amount of bacteria contained in the solution under a microscope to determine the bactericidal efficiency of the powder.
从测试结果看,BiOX(X=Cl,Br,I)降解有机污染物的能力优于纳米P25-TiO2,在紫外光响应下光解水产氢速率达到10~100μmol/h数量级,优于纳米P25-TiO2,BiOX也可以降解有害气体甲醛,杀除大肠杆菌和金黄色葡萄球菌的效果均优于纳米P25-TiO2。From the test results, the ability of BiOX (X=Cl, Br, I) to degrade organic pollutants is better than that of nano P25-TiO 2 , and the hydrogen production rate of photolysis water under ultraviolet light response reaches the order of 10-100 μmol/h, which is better than that of nano P25-TiO 2 , BiOX can also degrade harmful gas formaldehyde, and the effect of killing Escherichia coli and Staphylococcus aureus is better than that of nano-sized P25-TiO 2 .
附图说明 Description of drawings
图1为BiOX层状晶体结构;Figure 1 is the layered crystal structure of BiOX;
图2为BiOCl能带结构;Figure 2 is the energy band structure of BiOCl;
图3为BiOCl部分态密度及总的态密度;Figure 3 shows the partial density of states and the total density of states of BiOCl;
图4为BiOX(X=Cl,Br,I)紫外-可见吸收光谱;Fig. 4 is BiOX (X=Cl, Br, I) ultraviolet-visible absorption spectrum;
图5为BiOX(X=Cl,Br,I)和P25-TiO2光催化降解染料甲基橙的活性;Fig. 5 is BiOX (X=Cl, Br, I) and P25-TiO The activity of photocatalytic degradation dye methyl orange;
图6为实施例1制备的BiOCl的场发射扫描电镜图。6 is a field emission scanning electron microscope image of BiOCl prepared in Example 1.
具体实施方式 Detailed ways
下面介绍本发明的实施例,但本发明绝非限于实施例。Examples of the present invention will be described below, but the present invention is by no means limited to the examples.
实施例1:Example 1:
将Bi2O3粉末溶解于相应浓卤酸中,用稀氨水调节至pH=3,经过多次过滤直至检测不到X-离子(用硝酸银溶液检验)后,沉淀物在80℃烘干即得成品纳米光催化粉末。Dissolve the Bi 2 O 3 powder in the corresponding concentrated halogen acid, adjust the pH to 3 with dilute ammonia water, and filter it several times until no X-ions can be detected (tested with silver nitrate solution), and dry the precipitate at 80°C That is, the finished nanometer photocatalytic powder is obtained.
负载的BiOX(X=Cl,Br,I)光催化材料的具体过程可为:取2g BiOX(X=Cl,Br,I)催化剂粉末置入含有1OOml去离子水的烧杯中,加入10ml的甲醇空穴牺牲剂和适量的AgNO3或H2PtCl6·6H2O,强力搅拌的同时在300W汞灯85~10h,后经过多次过滤洗涤,干燥即得负载有纳米Ag或Pt颗粒的光催化材料。The specific process of the BiOX (X=Cl, Br, I) photocatalytic material of load can be: get 2g BiOX (X=Cl, Br, I) catalyst powder and insert in the beaker that contains 100ml deionized water, add the methanol of 10ml Hole sacrificial agent and an appropriate amount of AgNO 3 or H 2 PtCl 6 6H 2 O, while vigorously stirring in a 300W mercury lamp for 85-10 hours, after several times of filtration and washing, and drying to obtain a photon loaded with nano-Ag or Pt particles. catalytic material.
光催化降解有机物甲基橙的实验表明,BiOX(X=Cl,Br)的紫外光催化性能优于P25-TiO2,BiOX(X=Cl,Br,I)负载Ag纳米颗粒后光催化降解甲基橙(MO)效果提高;而负载相同质量分数的Pt的效果基本上同于Ag负载的情况。The photocatalytic degradation of methyl orange, an organic compound, shows that the UV photocatalytic performance of BiOX (X=Cl, Br) is better than that of P25-TiO 2 . The effect of base orange (MO) is improved; and the effect of loading the same mass fraction of Pt is basically the same as that of Ag loading.
在光催化裂解水产氢中,产氢速率均可以达到10μmol/h数量级,相同条件下产氢量顺序为:BiOCl>BiOBr>BiOI。负载Pt的效果优于负载Ag的情况,产氢速率均上升,达到100μmol/h数量级,产氢量顺序仍然为:BiOCl>BiOBr>BiOI。而纯的P25-TiO2则没有光催化裂解水产氢的能力。In the photocatalytic cracking of water for hydrogen production, the hydrogen production rate can reach the order of 10 μmol/h, and the order of hydrogen production under the same conditions is: BiOCl>BiOBr>BiOI. The effect of loading Pt is better than that of loading Ag, and the hydrogen production rate increases to the order of 100 μmol/h, and the order of hydrogen production is still: BiOCl>BiOBr>BiOI. However, pure P25-TiO 2 does not have the ability to photocatalytically split water to produce hydrogen.
在降解有机有害气体甲醛的实验中,光催化2h后,BiOX(X=Cl,Br,I)的降解率均超过了90%。降解率顺序为BiOCl>BiOBr>BiOI,而纯的P25-TiO2降解率为81%。In the experiment of degrading organic harmful gas formaldehyde, the degradation rate of BiOX (X=Cl, Br, I) exceeded 90% after photocatalysis for 2 hours. The order of degradation rate is BiOCl>BiOBr>BiOI, while the degradation rate of pure P25- TiO2 is 81%.
在杀菌实验中,光催化10h后,BiOX(X=Cl,Br,I)的杀菌率顺序为BiOCl>BiOBr>BiOI,杀菌率均超过了70%。而纯的P25-TiO2杀菌率为55%。In the bactericidal experiment, after 10 hours of photocatalysis, the order of the bactericidal rate of BiOX (X=Cl, Br, I) was BiOCl>BiOBr>BiOI, and the bactericidal rate exceeded 70%. And the pure P25-TiO 2 bactericidal rate is 55%.
实施例2:Example 2:
将化学计量比的Bi2O3和BiX3(X=Cl,Br,I)置于石英管中,抽真空后封装,在550℃加热12小时。冷却后开管研磨即得成品光催化粉末。The stoichiometric ratio of Bi 2 O 3 and BiX 3 (X=Cl, Br, I) was placed in a quartz tube, vacuumized, packaged, and heated at 550° C. for 12 hours. After cooling, open the tube and grind to get the finished photocatalytic powder.
光催化降解染料甲基橙,光解水产氢,降解有害物质甲醛和杀菌测试结果约为实施方式1中的40%左右,这可能是由于固相法制得的样品的比表面积较小造成的。Photocatalytic degradation of dye methyl orange, photolysis of water to produce hydrogen, degradation of harmful substance formaldehyde and bactericidal test results are about 40% of those in
实施例3:Example 3:
取100ml去离子水于烧杯中,用相应卤酸调节溶液pH小于1,然后将溶液加热至70℃左右,在不断搅拌的同时,缓慢加1mol硝酸铋-卤酸溶液,同时缓慢加入15%NaOH溶液以中和水解产生的HNO3,维持pH值在2左右,整个过程持续约1h。其间温度恒定在75℃左右,继续搅拌10min,冷却、过滤、洗涤、在80℃烘干即得成品光催化粉末。Take 100ml of deionized water in a beaker, adjust the pH of the solution to less than 1 with the corresponding halogen acid, then heat the solution to about 70°C, while stirring continuously, slowly add 1mol of bismuth nitrate-halogen acid solution, and at the same time slowly add 15% NaOH The solution is used to neutralize the HNO 3 produced by hydrolysis, and the pH value is maintained at about 2, and the whole process lasts for about 1 hour. During this period, the temperature was kept constant at about 75°C, continued to stir for 10 minutes, cooled, filtered, washed, and dried at 80°C to obtain the finished photocatalytic powder.
性能测试结果与实施例1基本相同。The performance test result is basically the same as that of Example 1.
实施例4:Example 4:
加入足量3mol卤酸、1mol固体硝酸铋、2wt%无水硫酸钠和1wt%十二烷基苯磺酸钠溶液,再加入75℃的热水搅拌得到透明的溶液,使总体积为200ml,然后放入微波炉中辐照2-3分钟,取出急冷,过滤、洗涤、在80℃烘干即得成品光催化粉末。Add a sufficient amount of 3mol halide acid, 1mol solid bismuth nitrate, 2wt% anhydrous sodium sulfate and 1wt% sodium dodecylbenzenesulfonate solution, then add hot water at 75°C and stir to obtain a transparent solution, making the total volume 200ml, Then put it into a microwave oven for 2-3 minutes of irradiation, take it out for rapid cooling, filter, wash, and dry at 80°C to obtain the finished photocatalytic powder.
性能测试结果略高于实施例1。Performance test result is slightly higher than
实施例5:Example 5:
取1mol硝酸铋溶于足量卤酸溶液,不断搅拌的同时加入2mol的相应卤化钠,然后用氨水调节pH为3,剧烈搅拌30min后,过滤、洗涤、在80℃烘干即得成品光催化粉末。Take 1mol of bismuth nitrate dissolved in a sufficient amount of halogen acid solution, add 2mol of the corresponding sodium halide while stirring constantly, then adjust the pH to 3 with ammonia water, stir vigorously for 30min, filter, wash, and dry at 80°C to obtain the finished photocatalyst powder.
性能测试结果与实施例1基本相同。The performance test result is basically the same as that of Example 1.
实施例6:Embodiment 6:
将1mol硝酸铋溶解于5mol冰醋酸中,搅拌的同时快速加入3mol碳酸钠和2mol卤化钠的混合溶液,剧烈搅拌30min后,过滤、洗涤、在80℃烘干即得成品光催化粉末。Dissolve 1 mol of bismuth nitrate in 5 mol of glacial acetic acid, quickly add a mixed solution of 3 mol of sodium carbonate and 2 mol of sodium halide while stirring, stir vigorously for 30 minutes, filter, wash, and dry at 80°C to obtain the finished photocatalytic powder.
性能测试结果与实施例1基本相同。The performance test result is basically the same as that of Example 1.
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