CN103212392B - A kind of method for preparing TiO2/diatomite composite photocatalytic material by sol-gel method - Google Patents
A kind of method for preparing TiO2/diatomite composite photocatalytic material by sol-gel method Download PDFInfo
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- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 title claims abstract description 44
- 230000001699 photocatalysis Effects 0.000 title claims abstract description 34
- 239000000463 material Substances 0.000 title claims abstract description 32
- 239000002131 composite material Substances 0.000 title claims abstract description 31
- 238000000034 method Methods 0.000 title claims abstract description 17
- 238000003980 solgel method Methods 0.000 title claims abstract description 13
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 title description 22
- 239000000725 suspension Substances 0.000 claims abstract description 39
- 229910010413 TiO 2 Inorganic materials 0.000 claims abstract description 36
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims abstract description 34
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims abstract description 34
- 238000003756 stirring Methods 0.000 claims abstract description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 26
- 239000008367 deionised water Substances 0.000 claims abstract description 24
- 229910021641 deionized water Inorganic materials 0.000 claims abstract description 24
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims abstract description 17
- 229960000583 acetic acid Drugs 0.000 claims abstract description 17
- FPCJKVGGYOAWIZ-UHFFFAOYSA-N butan-1-ol;titanium Chemical compound [Ti].CCCCO.CCCCO.CCCCO.CCCCO FPCJKVGGYOAWIZ-UHFFFAOYSA-N 0.000 claims abstract description 17
- 239000012362 glacial acetic acid Substances 0.000 claims abstract description 17
- 229910021645 metal ion Inorganic materials 0.000 claims abstract description 17
- 229910017604 nitric acid Inorganic materials 0.000 claims abstract description 17
- 238000001035 drying Methods 0.000 claims abstract description 10
- 229910000000 metal hydroxide Inorganic materials 0.000 claims abstract description 8
- 150000004692 metal hydroxides Chemical class 0.000 claims abstract description 8
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- 238000010438 heat treatment Methods 0.000 claims abstract description 5
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- 239000000203 mixture Substances 0.000 claims description 7
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- 229910052684 Cerium Inorganic materials 0.000 claims description 3
- 229910052782 aluminium Inorganic materials 0.000 claims description 3
- 229910052804 chromium Inorganic materials 0.000 claims description 3
- 229910052742 iron Inorganic materials 0.000 claims description 3
- 229910052746 lanthanum Inorganic materials 0.000 claims description 2
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims 3
- 230000015572 biosynthetic process Effects 0.000 claims 1
- 238000009413 insulation Methods 0.000 claims 1
- 238000013021 overheating Methods 0.000 claims 1
- 238000010521 absorption reaction Methods 0.000 abstract description 16
- OVYTZAASVAZITK-UHFFFAOYSA-M sodium;ethanol;hydroxide Chemical compound [OH-].[Na+].CCO OVYTZAASVAZITK-UHFFFAOYSA-M 0.000 abstract description 7
- 230000000694 effects Effects 0.000 abstract description 6
- 238000013033 photocatalytic degradation reaction Methods 0.000 abstract description 6
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- 239000000243 solution Substances 0.000 description 50
- 239000011941 photocatalyst Substances 0.000 description 6
- VCJMYUPGQJHHFU-UHFFFAOYSA-N iron(3+);trinitrate Chemical compound [Fe+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VCJMYUPGQJHHFU-UHFFFAOYSA-N 0.000 description 4
- 239000000843 powder Substances 0.000 description 4
- BNGXYYYYKUGPPF-UHFFFAOYSA-M (3-methylphenyl)methyl-triphenylphosphanium;chloride Chemical compound [Cl-].CC1=CC=CC(C[P+](C=2C=CC=CC=2)(C=2C=CC=CC=2)C=2C=CC=CC=2)=C1 BNGXYYYYKUGPPF-UHFFFAOYSA-M 0.000 description 3
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 3
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- 230000003197 catalytic effect Effects 0.000 description 2
- HSJPMRKMPBAUAU-UHFFFAOYSA-N cerium(3+);trinitrate Chemical compound [Ce+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O HSJPMRKMPBAUAU-UHFFFAOYSA-N 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 239000011651 chromium Substances 0.000 description 2
- PHFQLYPOURZARY-UHFFFAOYSA-N chromium trinitrate Chemical compound [Cr+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O PHFQLYPOURZARY-UHFFFAOYSA-N 0.000 description 2
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- FYDKNKUEBJQCCN-UHFFFAOYSA-N lanthanum(3+);trinitrate Chemical compound [La+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O FYDKNKUEBJQCCN-UHFFFAOYSA-N 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- WSFSSNUMVMOOMR-NJFSPNSNSA-N methanone Chemical compound O=[14CH2] WSFSSNUMVMOOMR-NJFSPNSNSA-N 0.000 description 1
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- 239000000126 substance Substances 0.000 description 1
- 239000004408 titanium dioxide Substances 0.000 description 1
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Abstract
本发明提供一种溶胶-凝胶法制备TiO2/硅藻土复合光催化材料的方法,属于环境污染治理、光催化功能材料制备技术领域。将钛酸丁酯加入到无水乙醇中,再加入冰醋酸,然后搅拌形成淡黄色透明的溶液A;取去离子水、硝酸加入到无水乙醇中制得透明的溶液B;将硅藻土加入到去离子水中搅拌成悬浮液,然后向悬浮液中加入金属硝酸盐溶液,再向其中加入氢氧化钠乙醇溶液,直至使金属离子转变为金属氢氧化物,形成混合悬浮液C;将溶液B和混合悬浮C依次加入到溶液A中,再静置陈化后形成凝胶;干燥后经过热处理即得到TiO2/硅藻土复合光催化材料。本方法简单、低成本、无二次污染,所得材料具有可见光活性、光催化降解率高和吸收边向可见光范围明显偏移。
The invention provides a method for preparing a TiO 2 /diatomite composite photocatalytic material by a sol-gel method, and belongs to the technical field of environmental pollution control and preparation of photocatalytic functional materials. Add butyl titanate to absolute ethanol, then add glacial acetic acid, and then stir to form light yellow transparent solution A; take deionized water and nitric acid and add it to absolute ethanol to obtain transparent solution B; diatomaceous earth Add it into deionized water and stir to form a suspension, then add metal nitrate solution to the suspension, and then add sodium hydroxide ethanol solution to it, until the metal ions are converted into metal hydroxides to form a mixed suspension C; the solution B and the mixed suspension C are added to the solution A in turn, and the gel is formed after standing and aging; after drying, the TiO 2 /diatomite composite photocatalytic material is obtained through heat treatment. The method is simple, low-cost, and has no secondary pollution, and the obtained material has visible light activity, high photocatalytic degradation rate and obvious shift of absorption edge to the visible light range.
Description
技术领域 technical field
本发明涉及一种溶胶-凝胶法制备TiO2/硅藻土复合光催化材料的方法,属于环境污染治理、光催化功能材料制备技术领域。 The invention relates to a method for preparing a TiO 2 /diatomite composite photocatalytic material by a sol-gel method, and belongs to the technical field of environmental pollution control and preparation of photocatalytic functional materials.
背景技术 Background technique
随着人类社会的进步,环境污染问题越来越严重,而这些污染物的除去需要消耗大量的能源,这给日益枯竭的能源提出严峻的挑战。如何合理的利用自然界中的有限资源,有效控制和解决环境污染问题,成为目前国际和国内众多学者研究的热点问题。近年来,备受关注的光催化技术可以将太阳能作为能源来降解环境中的污染物,但是,纯TiO2光催化剂自然光利用率不高;TiO2是一种宽禁带半导体,其锐钛矿型TiO2的禁带宽度为3.2ev,只有波长较短的紫外光(300~400nm)才能被其吸收和利用,太阳光中主要是可见光占43%,紫外光只占5%,这极大地限制了TiO2光催化剂的应用范围;而金红石型TiO2的禁带宽度(3.0eV)比锐钛矿型TiO2的窄,体相中金红石相增多时,光谱的吸收带边也相应地发生红移,可通过调控热处理温度的方法来控制金红石和锐钛矿的比例,从而使光谱的吸收带边发生相应地红移。 With the progress of human society, the problem of environmental pollution is becoming more and more serious, and the removal of these pollutants needs to consume a lot of energy, which poses a severe challenge to the increasingly depleted energy. How to rationally utilize the limited resources in nature and effectively control and solve the problem of environmental pollution has become a hot issue studied by many international and domestic scholars. In recent years, the photocatalytic technology that has attracted much attention can use solar energy as an energy source to degrade pollutants in the environment, but the natural light utilization rate of pure TiO 2 photocatalyst is not high; TiO 2 is a wide bandgap semiconductor, and its anatase The forbidden band width of type TiO 2 is 3.2ev, and only ultraviolet light (300-400nm) with a shorter wavelength can be absorbed and utilized by it. In sunlight, visible light mainly accounts for 43%, and ultraviolet light only accounts for 5%, which greatly Limits the scope of application of TiO2 photocatalyst; while the band gap (3.0eV) of rutile TiO2 is narrower than that of anatase TiO2 , when the rutile phase in the bulk phase increases, the absorption band edge of the spectrum also occurs accordingly Redshift, the ratio of rutile and anatase can be controlled by adjusting the heat treatment temperature, so that the absorption band edge of the spectrum will be redshifted accordingly.
我们可以采取两方法来解决TiO2光催化降解率不高的问题:一是通过掺杂金属离子。掺杂金属离子能给TiO2提供电予受体,有利于电子的转移,延长了电子与空穴的分离时间,降低了电子与空穴的复合,从而提高了TiO2的光催化降解率。二是二氧化钛负载在来源丰富、价格低廉和性质稳定的硅藻土为载体上。硅藻土是多孔性表面吸附剂,它和TiO2制备复合光催化剂可以更好地实现光生空穴的捕获,抑制电子—空穴对的复合;同时,硅藻土具有良好的吸附性能,不但能有效去除水中的有机污染物,降低光催化处理成本,还可将有机物吸附至TiO2晶粒表面,增加催化剂与污染物的接触几率,达到提高光降解效率,增大降解速率的目的。 We can take two methods to solve the problem of low photocatalytic degradation rate of TiO 2 : one is by doping metal ions. Doping metal ions can provide TiO 2 with electron acceptors, which is beneficial to the transfer of electrons, prolongs the separation time of electrons and holes, reduces the recombination of electrons and holes, and thus improves the photocatalytic degradation rate of TiO 2 . The second is that titanium dioxide is loaded on diatomite, which is rich in sources, low in price and stable in nature. Diatomite is a porous surface adsorbent, and it can better realize the capture of photogenerated holes and inhibit the recombination of electron-hole pairs by preparing a composite photocatalyst with TiO2 ; at the same time, diatomite has good adsorption properties, not only It can effectively remove organic pollutants in water, reduce the cost of photocatalytic treatment, and can also adsorb organic substances to the surface of TiO 2 grains, increasing the contact probability between catalysts and pollutants, achieving the purpose of improving photodegradation efficiency and increasing degradation rate.
发明内容 Contents of the invention
本发明针对目前TiO2光催化材料存在的问题,提出一种溶胶-凝胶法制备TiO2/硅藻土复合光催化材料的方法,这种TiO2/硅藻土复合光催化材料不仅通过将金属掺杂的TiO2负载在多孔的硅藻土上的方法来提高其光催化降解率,而且通过调控热处理温度的方法来控制金红石和锐钛矿的比例,从而提高其光催化活性和实现对可见光的吸收、利用。 The present invention aims at the existing problems of TiO 2 photocatalytic materials, and proposes a method for preparing TiO 2 /diatomite composite photocatalytic materials by sol-gel method. This TiO 2 /diatomite composite photocatalytic materials not only pass Metal-doped TiO 2 is loaded on porous diatomaceous earth to improve its photocatalytic degradation rate, and the ratio of rutile and anatase is controlled by adjusting the heat treatment temperature, thereby improving its photocatalytic activity and realizing Absorption and utilization of visible light.
本发明通过下列技术方案实现:一种溶胶-凝胶法制备TiO2/硅藻土复合光催化材料的方法,经过下列各步骤: The present invention is realized through the following technical solutions: a method for preparing TiO2 /diatomite composite photocatalytic material by a sol-gel method, through the following steps:
(1)按钛酸丁酯、无水乙醇和冰醋酸的体积比为20~28:48~54:2~8,将钛酸丁酯加入到无水乙醇中,再加入冰醋酸,然后搅拌20~50min形成淡黄色透明的溶液A; (1) According to the volume ratio of butyl titanate, absolute ethanol and glacial acetic acid as 20-28:48-54:2-8, add butyl titanate to absolute ethanol, then add glacial acetic acid, and then stir 20-50 minutes to form a light yellow and transparent solution A;
(2)按去离子水、硝酸和无水乙醇的体积比为8~13:1~3.5:47~55,取去离子水、硝酸加入到无水乙醇中制得透明的溶液B; (2) According to the volume ratio of deionized water, nitric acid and absolute ethanol as 8-13:1-3.5:47-55, add deionized water and nitric acid to absolute ethanol to prepare transparent solution B;
(3)将硅藻土加入到去离子水中搅拌成悬浮液,然后向悬浮液中加入浓度为1~10mol/L的金属硝酸盐溶液,混合搅拌均匀,使金属离子的质量浓度为0~5%,再向其中加入浓度为1~5mol/L的氢氧化钠乙醇溶液,直至使金属离子转变为金属氢氧化物,形成混合悬浮液C; (3) Add diatomite to deionized water and stir to form a suspension, then add metal nitrate solution with a concentration of 1 to 10 mol/L to the suspension, mix and stir evenly, so that the mass concentration of metal ions is 0 to 5 %, and then add a sodium hydroxide ethanol solution with a concentration of 1 to 5 mol/L until the metal ions are converted into metal hydroxides to form a mixed suspension C;
(4)按溶液A、溶液B和混合悬浮液C的体积比为78~82:58~64:105~114,将步骤(2)所得的溶液B和步骤(3)所得的混合悬浮C依次以0.1~1.0ml/min的速度加入到步骤(1)所得的溶液A中,并伴随搅拌0.5~1h,再静置陈化后形成凝胶; (4) According to the volume ratio of solution A, solution B and mixed suspension C of 78~82:58~64:105~114, the solution B obtained in step (2) and the mixed suspension C obtained in step (3) are sequentially Add it into the solution A obtained in step (1) at a rate of 0.1-1.0ml/min, and stir it for 0.5-1h, then let it stand for aging to form a gel;
(5)将步骤(4)所得凝胶进行干燥,干燥后经过热处理即得到TiO2/硅藻土复合光催化材料。 (5) Drying the gel obtained in step (4), and then heat-treating after drying to obtain a TiO 2 /diatomite composite photocatalytic material.
所得TiO2/硅藻土复合光催化材料待冷却到室温时,可按需要研磨成粉末状;并可按用户需要将其和室内涂料、增白剂混合涂在墙表面有去除甲醛等有害气体、具有防霉抗菌能力,也可将其粉末制品用来治理有机水污染领域。 When the obtained TiO 2 /diatomite composite photocatalytic material is cooled to room temperature, it can be ground into powder as required; and it can be mixed with interior paint and whitening agent and applied on the wall surface to remove formaldehyde and other harmful gases according to user needs. , It has anti-mildew and anti-bacterial ability, and its powder products can also be used to control the field of organic water pollution.
所述步骤(1)的钛酸丁酯、无水乙醇和冰醋酸均为市购分析纯。 The butyl titanate, absolute ethanol and glacial acetic acid in the step (1) are commercially available and of analytical grade. the
所述步骤(2)的硝酸和无水乙醇均为市购分析纯。 The nitric acid and absolute ethanol in the step (2) are commercially available analytically pure. the
所述步骤(3)的悬浮液是硅藻土与去离子水按固液比(g/mL)为1~20:100进行搅拌混合而成。 The suspension in the step (3) is formed by stirring and mixing diatomite and deionized water at a solid-to-liquid ratio (g/mL) of 1-20:100. the
所述步骤(3)的金属硝酸盐溶液为Fe、Cr、La、Ce和Al中的一种或多种的金属硝酸盐溶液。 The metal nitrate solution in the step (3) is a metal nitrate solution of one or more of Fe, Cr, La, Ce and Al. the
所述步骤(4)的静置陈化是在室温下陈化1~4h。 The standing aging in the step (4) is aging at room temperature for 1-4 hours. the
所述步骤(5)的干燥是在50~100℃下干燥1~5h。 The drying in the step (5) is at 50-100° C. for 1-5 hours. the
所述步骤(5)的热处理温度为500~700℃,保温1~6h。 The heat treatment temperature in the step (5) is 500-700° C., and the temperature is kept for 1-6 hours. the
本发明提供一种制备简单、低成本,且具有可见光活性、光催化降解率高和吸收带边向可见光范围明显偏移的TiO2/硅藻土复合光催化材料的制备方法。本方法制备简单、低成本、无二次污染,TiO2/硅藻土复合光催化材料具有可见光活性、光催化降解率高和吸收边向可见光范围明显偏移,具有优良的可见光光催化活性。所制的粉末催化剂可按用户需要将其和室内涂料、增白剂混合涂在内墙表面有去除甲醛等有害气体、具有防霉抗菌能力,可将其粉末制品用来治理有机水污染领域。 The invention provides a preparation method of TiO 2 /diatomite composite photocatalytic material with simple preparation, low cost, visible light activity, high photocatalytic degradation rate and obvious shift of absorption band edge to visible light range. The preparation method is simple, low-cost, and has no secondary pollution. The TiO 2 /diatomite composite photocatalytic material has visible light activity, high photocatalytic degradation rate and obvious shift of absorption edge to the visible light range, and has excellent visible light photocatalytic activity. The prepared powder catalyst can be mixed with indoor paint and whitening agent and coated on the surface of the inner wall according to the user's needs. It can remove harmful gases such as formaldehyde, and has anti-mildew and antibacterial capabilities. Its powder products can be used to treat organic water pollution.
附图说明 Description of drawings
图1为本发明的工艺流程示意图。 Fig. 1 is a schematic diagram of the process flow of the present invention. the
具体实施方式 Detailed ways
下面结合实施例对本发明做进一步描述。 The present invention will be further described below in conjunction with the examples. the
实施例1 Example 1
(1)按钛酸丁酯、无水乙醇和冰醋酸的体积比为25:50:5,将分析纯钛酸丁酯加入到分析纯无水乙醇中,再加入分析纯冰醋酸,然后搅拌30min形成淡黄色透明的溶液A; (1) According to the volume ratio of butyl titanate, absolute ethanol and glacial acetic acid as 25:50:5, add analytical pure butyl titanate to analytical pure absolute ethanol, then add analytical pure glacial acetic acid, and then stir 30min to form a light yellow transparent solution A;
(2)按去离子水、分析纯硝酸和分析纯无水乙醇的体积比为10:2:50,取去离子水、硝酸加入到无水乙醇中制得透明的溶液B; (2) According to the volume ratio of deionized water, analytically pure nitric acid and analytically pure absolute ethanol as 10:2:50, take deionized water and nitric acid and add them to absolute ethanol to obtain a transparent solution B;
(3)将硅藻土与去离子水按固液比(g/mL)为8:100进行搅拌成悬浮液,然后向悬浮液中加入1mL浓度为3mol/L的硝酸铁溶液,混合搅拌均匀,使金属离子的质量浓度为1%,再向其中加入浓度为5mol/L的氢氧化钠乙醇溶液,直至使金属离子转变为金属氢氧化物,形成混合悬浮液C; (3) Stir diatomaceous earth and deionized water at a solid-to-liquid ratio (g/mL) of 8:100 to form a suspension, then add 1 mL of ferric nitrate solution with a concentration of 3 mol/L to the suspension, mix and stir evenly , so that the mass concentration of metal ions is 1%, and then adding a sodium hydroxide ethanol solution with a concentration of 5mol/L to it, until the metal ions are converted into metal hydroxides to form a mixed suspension C;
(4)按溶液A、溶液B和混合悬浮液C的体积比为80:60:110,将步骤(2)所得的溶液B和步骤(3)所得的混合悬浮C依次以0.5ml/min的速度加入到步骤(1)所得的溶液A中,并伴随搅拌0.5h,再在室温下静置陈化2h后形成凝胶; (4) According to the volume ratio of solution A, solution B and mixed suspension C as 80:60:110, the solution B obtained in step (2) and the mixed suspension C obtained in step (3) are sequentially mixed at 0.5ml/min Add it to the solution A obtained in step (1) at a high speed, and stir for 0.5h, then leave it at room temperature for 2h to form a gel;
(5)将步骤(4)所得凝胶在100℃下进行干燥1h,干燥后经过600℃热处理并保温4h,即得到TiO2/硅藻土复合光催化材料。Fe-掺杂TiO2/硅藻土复合光催化材料的吸收带边向可见光范围明显偏移,禁带宽度为2.85eV,吸收带为423nm,表现出良好的可见光活性。 (5) The gel obtained in step (4) was dried at 100° C. for 1 hour, and then heat-treated at 600° C. and kept for 4 hours to obtain a TiO 2 /diatomite composite photocatalytic material. The absorption band edge of the Fe-doped TiO 2 /diatomite composite photocatalyst material is obviously shifted to the visible light range, the forbidden band width is 2.85eV, and the absorption band is 423nm, showing good visible light activity.
实施例2 Example 2
(1)按钛酸丁酯、无水乙醇和冰醋酸的体积比为20:48:2,将分析纯钛酸丁酯加入到分析纯无水乙醇中,再加入分析纯冰醋酸,然后搅拌20min形成淡黄色透明的溶液A; (1) According to the volume ratio of butyl titanate, absolute ethanol and glacial acetic acid as 20:48:2, add analytical pure butyl titanate to analytical pure absolute ethanol, then add analytical pure glacial acetic acid, and then stir 20min to form a light yellow transparent solution A;
(2)按去离子水、分析纯硝酸和分析纯无水乙醇的体积比为13:3.5:47,取去离子水、硝酸加入到无水乙醇中制得透明的溶液B; (2) According to the volume ratio of deionized water, analytically pure nitric acid and analytically pure absolute ethanol as 13:3.5:47, take deionized water and nitric acid and add them to absolute ethanol to prepare a transparent solution B;
(3)将硅藻土与去离子水按固液比(g/mL)为1:100进行搅拌成悬浮液,然后向悬浮液中加入浓度为1mol/L的硝酸镧溶液,混合搅拌均匀,使金属离子的质量浓度为0~5%,再向其中加入浓度为3mol/L的氢氧化钠乙醇溶液,直至使金属离子转变为金属氢氧化物,形成混合悬浮液C; (3) Stir diatomite and deionized water at a solid-to-liquid ratio (g/mL) of 1:100 to form a suspension, then add lanthanum nitrate solution with a concentration of 1mol/L to the suspension, mix and stir evenly, Make the mass concentration of metal ions 0-5%, and then add a sodium hydroxide ethanol solution with a concentration of 3mol/L to it until the metal ions are converted into metal hydroxides to form a mixed suspension C;
(4)按溶液A、溶液B和混合悬浮液C的体积比为78:58:105,将步骤(2)所得的溶液B和步骤(3)所得的混合悬浮C依次以1.0ml/min的速度加入到步骤(1)所得的溶液A中,并伴随搅拌0.8h,再在室温下静置陈化1h后形成凝胶; (4) According to the volume ratio of solution A, solution B and mixed suspension C of 78:58:105, the solution B obtained in step (2) and the mixed suspension C obtained in step (3) are sequentially mixed at 1.0ml/min Add it to the solution A obtained in step (1) at a high speed, and stir for 0.8h, and then stand and age at room temperature for 1h to form a gel;
(5)将步骤(4)所得凝胶在80℃下进行干燥3h,干燥后经过500℃热处理并保温6h,即得到TiO2/硅藻土复合光催化材料。La-掺杂TiO2/硅藻土复合光催化材料的吸收带边向可见光范围明显偏移,禁带宽度为3.03eV,吸收带为401nm,表现出一定的可见光活性。 (5) The gel obtained in step (4) was dried at 80° C. for 3 hours, and then heat-treated at 500° C. and kept for 6 hours after drying to obtain a TiO 2 /diatomite composite photocatalytic material. The absorption band edge of the La-doped TiO 2 /diatomite composite photocatalyst material shifts to the visible light range obviously, the forbidden band width is 3.03eV, and the absorption band is 401nm, showing certain visible light activity.
实施例3 Example 3
(1)按钛酸丁酯、无水乙醇和冰醋酸的体积比为28:54:8,将分析纯钛酸丁酯加入到分析纯无水乙醇中,再加入分析纯冰醋酸,然后搅拌50min形成淡黄色透明的溶液A; (1) According to the volume ratio of butyl titanate, absolute ethanol and glacial acetic acid as 28:54:8, add analytical pure butyl titanate to analytical pure absolute ethanol, then add analytical pure glacial acetic acid, and then stir 50min to form a light yellow transparent solution A;
(2)按去离子水、分析纯硝酸和分析纯无水乙醇的体积比为8:1:55,取去离子水、硝酸加入到无水乙醇中制得透明的溶液B; (2) According to the volume ratio of deionized water, analytically pure nitric acid and analytically pure absolute ethanol as 8:1:55, take deionized water and nitric acid and add them to absolute ethanol to obtain a transparent solution B;
(3)将硅藻土与去离子水按固液比(g/mL)为12:100进行搅拌成悬浮液,然后向悬浮液中加入浓度为6mol/L的金属硝酸铝溶液,混合搅拌均匀,使金属离子的质量浓度为0~5%,再向其中加入浓度为5mol/L的氢氧化钠乙醇溶液,直至使金属离子转变为金属氢氧化物,形成混合悬浮液C; (3) Stir diatomite and deionized water at a solid-to-liquid ratio (g/mL) of 12:100 to form a suspension, then add metal aluminum nitrate solution with a concentration of 6mol/L to the suspension, mix and stir evenly , so that the mass concentration of metal ions is 0 to 5%, and then adding a sodium hydroxide ethanol solution with a concentration of 5 mol/L to it, until the metal ions are converted into metal hydroxides to form a mixed suspension C;
(4)按溶液A、溶液B和混合悬浮液C的体积比为82:64:114,将步骤(2)所得的溶液B和步骤(3)所得的混合悬浮C依次以0.5ml/min的速度加入到步骤(1)所得的溶液A中,并伴随搅拌0.5h,再在室温下静置陈化3h后形成凝胶; (4) According to the volume ratio of solution A, solution B and mixed suspension C of 82:64:114, the solution B obtained in step (2) and the mixed suspension C obtained in step (3) are sequentially mixed at 0.5ml/min Add it to the solution A obtained in step (1) at a high speed, and stir it for 0.5h, then leave it to stand and age at room temperature for 3h to form a gel;
(5)将步骤(4)所得凝胶在50℃下进行干燥5h,干燥后经过650℃热处理并保温4h,即得到TiO2/硅藻土复合光催化材料。Al-掺杂TiO2/硅藻土复合光催化材料的吸收带边向可见光范围明显偏移,禁带宽度为3.06eV,吸收带为390nm,表现出一定的可见光活性。 (5) The gel obtained in step (4) was dried at 50° C. for 5 hours, and then heat-treated at 650° C. and kept for 4 hours to obtain a TiO 2 /diatomite composite photocatalytic material. The absorption band edge of the Al-doped TiO 2 /diatomite composite photocatalyst material shifts to the visible light range obviously, the forbidden band width is 3.06eV, and the absorption band is 390nm, showing certain visible light activity.
实施例4 Example 4
(1)按钛酸丁酯、无水乙醇和冰醋酸的体积比为23:52:7,将分析纯钛酸丁酯加入到分析纯无水乙醇中,再加入分析纯冰醋酸,然后搅拌30min形成淡黄色透明的溶液A; (1) According to the volume ratio of butyl titanate, absolute ethanol and glacial acetic acid as 23:52:7, add analytical pure butyl titanate to analytical pure absolute ethanol, then add analytical pure glacial acetic acid, and then stir 30min to form a light yellow transparent solution A;
(2)按去离子水、分析纯硝酸和分析纯无水乙醇的体积比为9:3.5:55,取去离子水、硝酸加入到无水乙醇中制得透明的溶液B; (2) According to the volume ratio of deionized water, analytically pure nitric acid and analytically pure absolute ethanol as 9:3.5:55, take deionized water and nitric acid and add them to absolute ethanol to obtain a transparent solution B;
(3)将硅藻土与去离子水按固液比(g/mL)为15:100进行搅拌成悬浮液,然后向悬浮液中加入0.5ml浓度为6mol/L硝酸铝和0.5ml浓度为3mol/L硝酸铁混合溶液,混合搅拌均匀,使金属离子的质量浓度为0~5%,再向其中加入浓度为5mol/L的氢氧化钠乙醇溶液,直至使金属离子转变为金属氢氧化物,形成混合悬浮液C; (3) Stir diatomite and deionized water at a solid-to-liquid ratio (g/mL) of 15:100 to form a suspension, then add 0.5ml of aluminum nitrate with a concentration of 6mol/L and 0.5ml of aluminum nitrate with a concentration of 3mol/L ferric nitrate mixed solution, mix and stir evenly, so that the mass concentration of metal ions is 0-5%, and then add sodium hydroxide ethanol solution with a concentration of 5mol/L to it, until the metal ions are transformed into metal hydroxides , forming a mixed suspension C;
(4)按溶液A、溶液B和混合悬浮液C的体积比为78:64:105,将步骤(2)所得的溶液B和步骤(3)所得的混合悬浮C依次以0.5ml/min的速度加入到步骤(1)所得的溶液A中,并伴随搅拌1h,再在室温下静置陈化2h后形成凝胶; (4) According to the volume ratio of solution A, solution B and mixed suspension C of 78:64:105, the solution B obtained in step (2) and the mixed suspension C obtained in step (3) are sequentially mixed at 0.5ml/min Add it to the solution A obtained in step (1) at a high speed, and stir it for 1 hour, then leave it to stand and age at room temperature for 2 hours to form a gel;
(5)将步骤(4)所得凝胶在60℃下进行干燥2h,干燥后经过700℃热处理并保温2h,即得到TiO2/硅藻土复合光催化材料。Al和Fe共掺杂TiO2/硅藻土复合光催化材料的吸收带边向可见光范围明显偏移,禁带宽度为2.72eV,吸收带为435nm,表现出明显的可见光催化活性。 (5) The gel obtained in step (4) was dried at 60°C for 2 hours, and then heat-treated at 700°C and kept for 2 hours after drying to obtain a TiO 2 /diatomite composite photocatalytic material. The absorption band edge of Al and Fe co-doped TiO 2 /diatomite composite photocatalytic material shifts to the visible light range obviously, the forbidden band width is 2.72eV, and the absorption band is 435nm, showing obvious visible light catalytic activity.
实施例5 Example 5
(1)按钛酸丁酯、无水乙醇和冰醋酸的体积比为28:48:6,将分析纯钛酸丁酯加入到分析纯无水乙醇中,再加入分析纯冰醋酸,然后搅拌50min形成淡黄色透明的溶液A; (1) According to the volume ratio of butyl titanate, absolute ethanol and glacial acetic acid as 28:48:6, add analytical pure butyl titanate to analytical pure absolute ethanol, then add analytical pure glacial acetic acid, and then stir 50min to form a light yellow transparent solution A;
(2)按去离子水、分析纯硝酸和分析纯无水乙醇的体积比为8:1:49,取去离子水、硝酸加入到无水乙醇中制得透明的溶液B; (2) According to the volume ratio of deionized water, analytically pure nitric acid and analytically pure absolute ethanol as 8:1:49, add deionized water and nitric acid to absolute ethanol to obtain a transparent solution B;
(3)将硅藻土与去离子水按固液比(g/mL)为20:100进行搅拌成悬浮液,然后向悬浮液中加入浓度为10mol/L的硝酸铬和硝酸铈溶液,混合搅拌均匀,使金属离子的质量浓度为0~5%,再向其中加入浓度为1mol/L的氢氧化钠乙醇溶液,直至使金属离子转变为金属氢氧化物,形成混合悬浮液C; (3) Stir diatomite and deionized water at a solid-to-liquid ratio (g/mL) of 20:100 to form a suspension, then add chromium nitrate and cerium nitrate solutions with a concentration of 10mol/L to the suspension, and mix Stir evenly so that the mass concentration of metal ions is 0-5%, and then add sodium hydroxide ethanol solution with a concentration of 1mol/L to it until the metal ions are converted into metal hydroxides to form a mixed suspension C;
(4)按溶液A、溶液B和混合悬浮液C的体积比为82:62:110,将步骤(2)所得的溶液B和步骤(3)所得的混合悬浮C依次以0.1ml/min的速度加入到步骤(1)所得的溶液A中,并伴随搅拌1h,再在室温下静置陈化4h后形成凝胶; (4) According to the volume ratio of solution A, solution B and mixed suspension C of 82:62:110, the solution B obtained in step (2) and the mixed suspension C obtained in step (3) are sequentially mixed at 0.1ml/min Add it to the solution A obtained in step (1) at a high speed, and stir it for 1 hour, and then leave it at room temperature for 4 hours to form a gel;
(5)将步骤(4)所得凝胶在100℃下进行干燥3h,干燥后经过700℃热处理并保温1h,即得到TiO2/硅藻土复合光催化材料。Cr和Ce共掺杂TiO2/硅藻土复合光催化材料的吸收带边向可见光范围明显偏移,禁带宽度为2.92eV,吸收带为405nm,表现出明显的可见光催化活性。 (5) The gel obtained in step (4) was dried at 100°C for 3 hours, and after drying, it was heat-treated at 700°C and kept for 1 hour to obtain a TiO 2 /diatomite composite photocatalytic material. The absorption band edge of the Cr and Ce co-doped TiO 2 /diatomite composite photocatalytic material shifts to the visible light range obviously, the forbidden band width is 2.92eV, and the absorption band is 405nm, showing obvious visible light catalytic activity.
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