CN104888858B - A kind of ternary high efficiency composition visible-light photocatalysis material and preparation method thereof - Google Patents
A kind of ternary high efficiency composition visible-light photocatalysis material and preparation method thereof Download PDFInfo
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- 238000002360 preparation method Methods 0.000 title claims abstract description 13
- 238000007146 photocatalysis Methods 0.000 title claims abstract description 7
- 239000000203 mixture Substances 0.000 title claims description 12
- 239000013207 UiO-66 Substances 0.000 claims abstract description 40
- 239000011941 photocatalyst Substances 0.000 claims abstract description 32
- 239000011218 binary composite Substances 0.000 claims abstract description 17
- 239000003054 catalyst Substances 0.000 claims abstract description 8
- KKEYFWRCBNTPAC-UHFFFAOYSA-N Terephthalic acid Chemical compound OC(=O)C1=CC=C(C(O)=O)C=C1 KKEYFWRCBNTPAC-UHFFFAOYSA-N 0.000 claims description 12
- WPYMKLBDIGXBTP-UHFFFAOYSA-N benzoic acid Chemical compound OC(=O)C1=CC=CC=C1 WPYMKLBDIGXBTP-UHFFFAOYSA-N 0.000 claims description 11
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 8
- 239000000243 solution Substances 0.000 claims description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 7
- 239000005711 Benzoic acid Substances 0.000 claims description 5
- 239000007864 aqueous solution Substances 0.000 claims description 5
- 235000010233 benzoic acid Nutrition 0.000 claims description 5
- 238000003756 stirring Methods 0.000 claims description 5
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 claims description 4
- 238000006243 chemical reaction Methods 0.000 claims description 4
- ZNCPFRVNHGOPAG-UHFFFAOYSA-L sodium oxalate Chemical compound [Na+].[Na+].[O-]C(=O)C([O-])=O ZNCPFRVNHGOPAG-UHFFFAOYSA-L 0.000 claims description 4
- 229940039790 sodium oxalate Drugs 0.000 claims description 4
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 3
- 239000004202 carbamide Substances 0.000 claims description 3
- 230000015556 catabolic process Effects 0.000 claims description 3
- 238000006731 degradation reaction Methods 0.000 claims description 3
- 229910017604 nitric acid Inorganic materials 0.000 claims description 3
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N titanium dioxide Inorganic materials O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 3
- 229910052799 carbon Inorganic materials 0.000 claims description 2
- 238000000227 grinding Methods 0.000 claims description 2
- 238000002156 mixing Methods 0.000 claims description 2
- 229910020470 K2Ti4O9 Inorganic materials 0.000 claims 8
- 238000005406 washing Methods 0.000 claims 3
- 229910007932 ZrCl4 Inorganic materials 0.000 claims 2
- 238000007792 addition Methods 0.000 claims 1
- 150000001336 alkenes Chemical class 0.000 claims 1
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- 238000009833 condensation Methods 0.000 claims 1
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- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Substances [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 claims 1
- 229910000027 potassium carbonate Inorganic materials 0.000 claims 1
- 239000002131 composite material Substances 0.000 abstract description 27
- 238000001179 sorption measurement Methods 0.000 abstract description 9
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- 230000004298 light response Effects 0.000 abstract description 3
- 238000000034 method Methods 0.000 abstract description 3
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- 238000004729 solvothermal method Methods 0.000 abstract 1
- 239000010936 titanium Substances 0.000 description 70
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical compound CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 description 13
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- 238000002441 X-ray diffraction Methods 0.000 description 6
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- PYWVYCXTNDRMGF-UHFFFAOYSA-N rhodamine B Chemical compound [Cl-].C=12C=CC(=[N+](CC)CC)C=C2OC2=CC(N(CC)CC)=CC=C2C=1C1=CC=CC=C1C(O)=O PYWVYCXTNDRMGF-UHFFFAOYSA-N 0.000 description 4
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- JYEUMXHLPRZUAT-UHFFFAOYSA-N 1,2,3-triazine Chemical group C1=CN=NN=C1 JYEUMXHLPRZUAT-UHFFFAOYSA-N 0.000 description 1
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- NJLLQSBAHIKGKF-UHFFFAOYSA-N dipotassium dioxido(oxo)titanium Chemical compound [K+].[K+].[O-][Ti]([O-])=O NJLLQSBAHIKGKF-UHFFFAOYSA-N 0.000 description 1
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Abstract
本发明公开了一种三元高效复合可见光光催化剂及其制备方法和应用,其特征在于:通过煅烧法制备N‑K2Ti4O9和g‑C3N4,通过静电吸引制备N‑K2Ti4O9/g‑C3N4二元复合材料,进而利用溶剂热法自组装合成N‑K2Ti4O9/g‑C3N4/UiO‑66三元高效复合可见光光催化剂。本发明利用N‑K2Ti4O9的可见光响应好、g‑C3N4传导电子空穴能力强、UiO‑66具有MOF材料吸附量大的特点,综合三者优点合成的三元复合光催化剂在复合促进的光生电荷分离作用下,具有显著增强的可见光下光催化降解有机染料活性,在光催化领域具有广阔的应用前景。
The invention discloses a ternary high-efficiency composite visible light photocatalyst and its preparation method and application, which are characterized in that N-K 2 Ti 4 O 9 and g-C 3 N 4 are prepared by a calcination method, and N-K 2 Ti 4 O 9 and g-C 3 N 4 are prepared by electrostatic attraction. K 2 Ti 4 O 9 /g‑C 3 N 4 binary composite material, and then self-assembled into N‑K 2 Ti 4 O 9 /g‑C 3 N 4 /UiO‑66 ternary high-efficiency composite visible light by solvothermal method catalyst of light. In the present invention, N-K 2 Ti 4 O 9 has a good visible light response, g-C 3 N 4 has a strong ability to conduct electrons and holes, and UiO-66 has the characteristics of large adsorption capacity of MOF materials, and combines the advantages of the three components to synthesize a ternary compound Under the action of recombination-promoted separation of photogenerated charges, photocatalysts have significantly enhanced photocatalytic degradation activity of organic dyes under visible light, and have broad application prospects in the field of photocatalysis.
Description
技术领域technical field
本发明属于材料制备、可见光光催化技术、环境保护领域,具体涉及三元高效复合光催化剂N-K2Ti4O9/g-C3N4/UiO-66的制备及其在可见光下催化降解水中有机污染物的应用。The invention belongs to the fields of material preparation, visible light photocatalysis technology and environmental protection, and specifically relates to the preparation of ternary high-efficiency composite photocatalyst NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 and its catalytic degradation of organic pollution in water under visible light application of things.
背景技术Background technique
当今能源短缺、环境污染问题越来越引起人们的关注,人类社会的可持续发展面临巨大的挑战。光催化技术是降解环境污染物的一种新型处理技术,具有低碳、洁净、环保等优点,因此是解决能源、环境问题的一种理想途径,然而传统的二氧化钛等光催化剂由于带隙高、光生电子-空穴复合速率快等缺点,限制了光催化技术的实际应用,如何制备高效的光催化剂则是光催化技术应用需要解决的一个关键问题。Today's energy shortages and environmental pollution have attracted more and more attention, and the sustainable development of human society is facing enormous challenges. Photocatalytic technology is a new treatment technology for degrading environmental pollutants. It has the advantages of low-carbon, clean, and environmentally friendly. Therefore, it is an ideal way to solve energy and environmental problems. However, traditional photocatalysts such as titanium dioxide have high band gaps, The shortcomings of photogenerated electron-hole recombination rate and other shortcomings limit the practical application of photocatalytic technology. How to prepare high-efficiency photocatalyst is a key problem that needs to be solved in the application of photocatalytic technology.
钛酸钾(K2Ti4O9)被普遍认为是一种可靠的材料,缘于其无毒、性质稳定、材料易得、光电性质独特等性能。然而由于其带隙能较高(3.2-3.4eV),只能被紫外光激发,因此提高其光催化活性以拓宽相关材料的应用范围具有重要意义。将氮元素掺杂到K2Ti4O9中(标记为“N-K2Ti4O9”)是减少带隙的一种普遍方法,掺杂后光催化活性得到提高,但是N-K2Ti4O9等低带隙半导体普遍存在比表面积小、对疏水性有机物吸附差和单一材料存在光生电子-空穴复合速率快等缺陷,而限制了其光催化性能的进一步提高。g-C3N4是由三氮杂苯单元构成的聚合物,是非金属半导体,其热稳定性和化学稳定性较强,有离域共轭π键(可以有效的传导光生载流子),在可见光催化反应方面主要用于光解水及有机污染物的降解等,但是g-C3N4光催化剂也存在比表面积小,光生载流子复合严重等缺点。研究发现,对g-C3N4进行酸处理可以提高其比表面积,促进电荷分离。而且g-C3N4经过酸处理其氮原子质子化使其带正电,容易和其他带负电的材料通过静电吸引有效复合在一起。金属有机框架(metal-organic framework,简称MOF)材料是近十几年来才引起广泛关注的新型多孔材料,是由氧、氮等多齿有机配体与过渡金属离子自组装而成的配位聚合物,具有特别大的比表面积(多数MOF的比表面积在1000m2/g以上,大于常规的多孔材料)。其敞口贯通的孔道有利于吸附浓缩环境中的污染物分子到材料的表面和内部。其中UiO-66是ZrIV和对苯二甲酸配位反应形成的一种MOF材料,具有比表面积和吸附量大,物理和化学性质稳定等优点。鉴于UiO-66优异的吸附性能,将其负载到其他材料表面形成复合结构,能够提高材料的吸附光催化性能。Potassium titanate (K 2 Ti 4 O 9 ) is generally regarded as a reliable material due to its non-toxic, stable properties, easy availability of materials, and unique photoelectric properties. However, due to its high band gap energy (3.2-3.4eV), it can only be excited by ultraviolet light, so it is of great significance to improve its photocatalytic activity to broaden the application range of related materials. Doping nitrogen into K 2 Ti 4 O 9 (marked as "NK 2 Ti 4 O 9 ") is a common method to reduce the band gap, and the photocatalytic activity is improved after doping, but NK 2 Ti 4 O 9 and other low-bandgap semiconductors generally have defects such as small specific surface area, poor adsorption of hydrophobic organic substances, and fast photogenerated electron-hole recombination rate in a single material, which limits the further improvement of its photocatalytic performance. gC 3 N 4 is a polymer composed of triazine units. It is a non-metallic semiconductor with strong thermal and chemical stability. It has delocalized conjugated π bonds (which can effectively conduct photogenerated carriers). Visible light catalysis is mainly used for photolysis of water and degradation of organic pollutants, etc. However, gC 3 N 4 photocatalyst also has disadvantages such as small specific surface area and serious recombination of photogenerated carriers. The study found that acid treatment of gC 3 N 4 can increase its specific surface area and promote charge separation. Moreover, gC 3 N 4 is acid-treated and its nitrogen atom is protonated to make it positively charged, and it is easy to effectively recombine with other negatively charged materials through electrostatic attraction. Metal-organic framework (MOF) material is a new type of porous material that has attracted widespread attention in the past ten years. It has a particularly large specific surface area (the specific surface area of most MOFs is above 1000m 2 /g, which is larger than conventional porous materials). Its open and through pores are conducive to the adsorption of pollutant molecules in the concentrated environment to the surface and interior of the material. Among them, UiO-66 is a MOF material formed by the coordination reaction of Zr IV and terephthalic acid, which has the advantages of large specific surface area and adsorption capacity, and stable physical and chemical properties. In view of the excellent adsorption performance of UiO-66, loading it on the surface of other materials to form a composite structure can improve the adsorption photocatalytic performance of the material.
本发明结合N-K2Ti4O9可见光响应好、g-C3N4传导电子空穴能力强、MOF材料吸附量大的优点,制备出的N-K2Ti4O9/g-C3N4/UiO-66三元复合材料具有较高的吸附性能,能有效分离光生电子-空穴对,有显著增强的可见光光催化活性。The present invention combines the advantages of good visible light response of NK 2 Ti 4 O 9 , strong ability of gC 3 N 4 to conduct electrons and holes, and large adsorption capacity of MOF materials to prepare NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 The ternary composite material has high adsorption performance, can effectively separate photogenerated electron-hole pairs, and has significantly enhanced visible light photocatalytic activity.
发明内容Contents of the invention
本发明的目的是提供一种N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂及其制备方法,以克服单一催化材料存在的缺陷并通过复合促进光生电荷分离作用,其制备方法简单,降解罗丹明B的光催化效果显著。The purpose of the present invention is to provide a NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst and its preparation method to overcome the defects of a single catalytic material and promote the separation of photogenerated charges by composite The preparation method is simple, and the photocatalytic effect of degrading rhodamine B is remarkable.
为实现上述目的,本发明采用如下技术方案:To achieve the above object, the present invention adopts the following technical solutions:
本发明三元高效复合可见光光催化剂,其特点在于:所述三元高效复合可见光光催化剂由N-K2Ti4O9、g-C3N4和UiO-66复合构成,记为N-K2Ti4O9/g-C3N4/UiO-66。The ternary high-efficiency composite visible light photocatalyst of the present invention is characterized in that: the ternary high-efficiency composite visible light photocatalyst is composed of NK 2 Ti 4 O 9 , gC 3 N 4 and UiO-66, denoted as NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66.
本发明三元高效复合可见光光催化剂的制备方法,其特点在于:The preparation method of the ternary high-efficiency composite visible light photocatalyst of the present invention is characterized in that:
(1)将K2CO3与TiO2按摩尔比1:9~4:9混合并研磨均匀,然后在400~1000℃煅烧4~10h,最后自然冷却至室温,获得K2Ti4O9;(1) Mix K 2 CO 3 and TiO 2 in a molar ratio of 1:9-4:9 and grind them evenly, then calcinate at 400-1000°C for 4-10 hours, and finally cool naturally to room temperature to obtain K 2 Ti 4 O 9 ;
将K2Ti4O9和尿素按质量比1:5~3:5混合后,在300~500℃煅烧3~6h,然后自然冷却至室温,获得N-K2Ti4O9;After mixing K 2 Ti 4 O 9 and urea at a mass ratio of 1:5 to 3:5, calcining at 300 to 500°C for 3 to 6 hours, and then naturally cooling to room temperature to obtain NK 2 Ti 4 O 9 ;
将N-K2Ti4O9加入到浓度为0.10~0.30mol/L的草酸钠水溶液中,搅拌、超声,然后过滤、洗涤、干燥、研磨,获得预处理N-K2Ti4O9;Add NK 2 Ti 4 O 9 to an aqueous solution of sodium oxalate with a concentration of 0.10-0.30 mol/L, stir, sonicate, then filter, wash, dry, and grind to obtain pretreated NK 2 Ti 4 O 9 ;
(2)将三聚氰胺在400~600℃煅烧3~8h,然后冷却至室温、研磨,获得g-C3N4;(2) Calcining melamine at 400-600°C for 3-8 hours, then cooling to room temperature and grinding to obtain gC 3 N 4 ;
将所述g-C3N4加入到浓度为0.5~2.0mol/L的硝酸溶液中,并在135℃下保温6h,将所得样品洗涤至中性、干燥,获得预处理g-C3N4;The gC 3 N 4 was added to a nitric acid solution with a concentration of 0.5-2.0 mol/L, and kept at 135°C for 6 hours, and the obtained sample was washed until neutral and dried to obtain pretreated gC 3 N 4 ;
(3)将步骤(1)所获得的预处理N-K2Ti4O9和步骤(2)所获得的预处理g-C3N4按质量比为1:2~7:2混合于乙醇中,然后搅拌20~40h,过滤,洗涤,干燥,获得N-K2Ti4O9/g-C3N4二元复合材料;(3) Mix the pretreated NK 2 Ti 4 O 9 obtained in step (1) and the pretreated gC 3 N 4 obtained in step (2) in ethanol at a mass ratio of 1:2 to 7:2, and then Stir for 20-40 hours, filter, wash, and dry to obtain NK 2 Ti 4 O 9 /gC 3 N 4 binary composite material;
(4)将步骤(3)所获得的N-K2Ti4O9/g-C3N4二元复合材料与ZrCl4按质量比1:2~7:2加入到N,N-二甲基甲酰胺中,然后加入对苯二甲酸和苯甲酸(对苯二甲酸、ZrCl4和苯甲酸的质量比为0.64:1:10),超声30min后将其转移至聚四氟乙烯反应釜中在100~150℃反应18~32h,所得产物经过滤、洗涤、干燥,即获得N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂。(4) Add the NK 2 Ti 4 O 9 /gC 3 N 4 binary composite material and ZrCl 4 obtained in step (3) to N,N-dimethylformamide at a mass ratio of 1:2 to 7:2 In, then add terephthalic acid and benzoic acid (the mass ratio of terephthalic acid, ZrCl 4 and benzoic acid is 0.64:1:10), it is transferred to polytetrafluoroethylene reactor after ultrasonic 30min in 100~ After reacting at 150°C for 18-32 hours, the obtained product was filtered, washed and dried to obtain NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst.
本发明还公开了上述三元高效复合可见光光催化剂作为可见光光催化降解水溶液中有机污染物的催化剂的应用。The invention also discloses the application of the above ternary high-efficiency composite visible light photocatalyst as a catalyst for visible light photocatalytic degradation of organic pollutants in aqueous solution.
本发明的有益效果体现在:The beneficial effects of the present invention are reflected in:
(1)本发明首次将复合光催化剂N-K2Ti4O9/g-C3N4/UiO-66应用于光催化领域,是一种新型的降解有机污染物的光催化剂,制备方法简单易行,可见光催化效率高,在光催化领域具有广阔的应用前景;(1) The present invention applies the composite photocatalyst NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 to the field of photocatalysis for the first time. It is a new type of photocatalyst for degrading organic pollutants. The preparation method is simple and feasible. Visible light catalytic efficiency is high, and it has broad application prospects in the field of photocatalysis;
(2)本发明通过修饰诱导的静电吸引制备N-K2Ti4O9/g-C3N4二元复合材料,进而利用配位反应组装制备N-K2Ti4O9/g-C3N4/UiO-66三元复合材料,用于协同光催化净化水中有机污染物;(2) The present invention prepares NK 2 Ti 4 O 9 /gC 3 N 4 binary composites through modification-induced electrostatic attraction, and then utilizes coordination reaction assembly to prepare NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 Ternary composite materials for synergistic photocatalytic purification of organic pollutants in water;
(3)本发明结合N-K2Ti4O9可见光响应好,薄层状g-C3N4容易和其他材料结合且传导电子空穴能力强,UiO-66吸附量大的优势,复合不仅增大了催化剂的比表面积,还提高了光生载流子的分离效率和光催化效率。(3) The present invention combines the advantages of good visible light response of NK 2 Ti 4 O 9 , thin-layered gC 3 N 4 is easy to combine with other materials and has a strong ability to conduct electrons and holes, and the advantages of large adsorption amount of UiO-66. The combination not only increases The specific surface area of the catalyst also improves the separation efficiency and photocatalytic efficiency of photogenerated carriers.
附图说明Description of drawings
图1是本发明N-K2Ti4O9、g-C3N4和UiO-66、N-K2Ti4O9/g-C3N4二元复合材料和N-K2Ti4O9/g-C3N4/UiO-66(3:2)三元高效复合可见光光催化剂的XRD图;Figure 1 is the present invention NK 2 Ti 4 O 9 , gC 3 N 4 and UiO-66, NK 2 Ti 4 O 9 /gC 3 N 4 binary composites and NK 2 Ti 4 O 9 /gC 3 N 4 /UiO XRD pattern of -66(3:2) ternary high-efficiency composite visible light photocatalyst;
图2是本发明UiO-66(a)、N-K2Ti4O9(b)、g-C3N4(c)和N-K2Ti4O9/g-C3N4/UiO-66(3:2)三元高效复合可见光光催化剂(d)的TEM图;Fig. 2 is UiO-66 (a), NK 2 Ti 4 O 9 (b), gC 3 N 4 (c) and NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 (3:2) of the present invention TEM image of ternary high-efficiency composite visible light photocatalyst (d);
图3是本发明N-K2Ti4O9、g-C3N4、UiO-66、N-K2Ti4O9/g-C3N4二元复合材料和N-K2Ti4O9/g-C3N4/UiO-66(3:2)三元高效复合可见光光催化剂对罗丹明B的可见光催化效果图;Fig. 3 shows NK 2 Ti 4 O 9 , gC 3 N 4 , UiO-66, NK 2 Ti 4 O 9 /gC 3 N 4 binary composites and NK 2 Ti 4 O 9 /gC 3 N 4 /UiO of the present invention -66 (3:2) ternary high-efficiency composite visible light photocatalyst for visible light photocatalysis of Rhodamine B;
图4是本发明不同比例的N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂对罗丹明B的可见光催化效果图。Fig. 4 is a visible light photocatalytic effect diagram of different ratios of NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst on rhodamine B in the present invention.
具体实施方式detailed description
下面列举实施例进一步说明本发明。The following examples are given to further illustrate the present invention.
实施例1Example 1
本实施例按如下步骤制备N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂:In this example, NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst was prepared according to the following steps:
1、N-K2Ti4O9的制备1. Preparation of NK 2 Ti 4 O 9
将6.6g K2CO3与12.0g TiO2(摩尔比为1:3)混合放入研钵中,研磨充分后,将粉末放入坩埚,在150℃下煅烧2h,然后升温至960℃,煅烧10h,冷却后,得到K2Ti4O9;Mix 6.6g K 2 CO 3 and 12.0g TiO 2 (molar ratio 1:3) into a mortar, grind the powder thoroughly, put the powder into a crucible, calcinate at 150°C for 2h, then raise the temperature to 960°C, Calcined for 10h, after cooling, K 2 Ti 4 O 9 was obtained;
将1.0g K2Ti4O9和2.0g尿素于15g乙醇中混合,再加热将溶剂蒸发,移至马弗炉中400℃煅烧4h,冷却、水洗、干燥得到N-K2Ti4O9。所得N-K2Ti4O9的XRD图如图1所示,TEM图如图2(b)所示。Mix 1.0g K 2 Ti 4 O 9 and 2.0g urea in 15g ethanol, heat to evaporate the solvent, move to a muffle furnace for calcination at 400°C for 4 hours, cool, wash with water, and dry to obtain NK 2 Ti 4 O 9 . The XRD pattern of the obtained NK 2 Ti 4 O 9 is shown in Fig. 1, and the TEM pattern is shown in Fig. 2(b).
2、N-K2Ti4O9预处理2. NK 2 Ti 4 O 9 pretreatment
将步骤1得到的N-K2Ti4O9加入到100mL的草酸钠水溶液(0.22mol·L-1)中,搅拌2h,超声1h后,过滤、水洗、70℃干燥5h、研磨后得到预处理N-K2Ti4O9。Add the NK 2 Ti 4 O 9 obtained in Step 1 into 100 mL of sodium oxalate aqueous solution (0.22 mol L -1 ), stir for 2 h, ultrasonicate for 1 h, filter, wash with water, dry at 70°C for 5 h, and grind to obtain pretreated NK 2 Ti 4 O 9 .
3、g-C3N4的制备3. Preparation of gC 3 N 4
将5.0g三聚氰胺放入坩埚中,移至马弗炉中以每分钟3℃的升温速度加热至520℃,并保温4小时,然后冷却至室温、研磨,得到g-C3N4。所得g-C3N4的XRD图如图1所示,TEM图如图2(c)所示。Put 5.0g of melamine into a crucible, move it to a muffle furnace, heat it up to 520°C at a rate of 3°C per minute, keep it warm for 4 hours, then cool to room temperature and grind to obtain gC 3 N 4 . The XRD pattern of the obtained gC 3 N 4 is shown in Figure 1, and the TEM image is shown in Figure 2(c).
4、g-C3N4的氮质子化4. Nitrogen protonation of gC 3 N 4
将步骤3得到的g-C3N4放入硝酸(0.5mol·L-1)溶液中,移至聚四氟乙烯反应釜中135℃下保温6h。取出样品,将样品洗涤至中性,70℃干燥5h,得到预处理g-C3N4。The gC 3 N 4 obtained in Step 3 was put into a nitric acid (0.5 mol·L -1 ) solution, and transferred to a polytetrafluoroethylene reactor at 135° C. for 6 h. The sample was taken out, washed until neutral, and dried at 70°C for 5 hours to obtain pretreated gC 3 N 4 .
5、N-K2Ti4O9/g-C3N4二元复合光催化剂的制备5. Preparation of NK 2 Ti 4 O 9 /gC 3 N 4 binary composite photocatalyst
将1.0g步骤2中所得的预处理N-K2Ti4O9和0.5g步骤4中所得的预处理g-C3N4于50mL乙醇溶液中混合搅拌24h,过滤,洗涤,干燥得到N-K2Ti4O9/g-C3N4二元复合材料。所得N-K2Ti4O9/g-C3N4二元复合材料的XRD图如图1所示。1.0g of the pretreated NK 2 Ti 4 O 9 obtained in step 2 and 0.5g of the pretreated gC 3 N 4 obtained in step 4 were mixed and stirred in 50mL ethanol solution for 24h, filtered, washed, and dried to obtain NK 2 Ti 4 O 9 /gC 3 N 4 binary composites. The XRD pattern of the obtained NK 2 Ti 4 O 9 /gC 3 N 4 binary composite is shown in FIG. 1 .
6、N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂的制备6. Preparation of NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst
称取0.080g步骤5中制备出的N-K2Ti4O9/g-C3N4二元复合材料、0.053g ZrCl4、0.034g对苯二甲酸及0.530g苯甲酸加入到42ml的N,N-二甲基甲酰胺中,然后超声30min后将其转移至50mL聚四氟乙烯反应釜中120℃反应24h,然后冷却至室温,过滤并用DMF和CHCl3各洗涤数次,减压干燥得到三元高效复合可见光光催化剂N-K2Ti4O9/g-C3N4/UiO-66(3:2)(即N-K2Ti4O9/g-C3N4二元复合材料与ZrCl4的质量比为3:2)。Weigh 0.080g of the NK 2 Ti 4 O 9 /gC 3 N 4 binary composite material prepared in step 5, 0.053g of ZrCl 4 , 0.034g of terephthalic acid and 0.530g of benzoic acid and add it to 42ml of N,N- Dimethylformamide, then sonicated for 30min, transferred to a 50mL polytetrafluoroethylene reactor at 120°C for 24h, then cooled to room temperature, filtered and washed several times with DMF and CHCl3 , dried under reduced pressure to obtain ternary Efficient composite visible light photocatalyst NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 (3:2) (that is, the mass ratio of NK 2 Ti 4 O 9 /gC 3 N 4 binary composite to ZrCl 4 is 3 :2).
所得产物的XRD图如图1所示,TEM图如图2(d)所示。The XRD pattern of the obtained product is shown in Figure 1, and the TEM image is shown in Figure 2(d).
为进行光催化性能的对比,本实施例还按如下步骤制备了UiO-66:In order to compare the photocatalytic performance, this example also prepared UiO-66 according to the following steps:
称取0.053g ZrCl4(0.227mmol)、0.034g对苯二甲酸(0.227mmol)和0.530g苯甲酸(4.344mmol)加入到25ml的N,N-二甲基甲酰胺中,然后超声30min后将其转移至30ml聚四氟乙烯反应釜中120℃反应24h,反应过后冷却至室温,过滤并用DMF和CHCl3各洗涤数次,减压干燥得到UiO-66。所得UiO-66的XRD图如图1所示,TEM图如图2(a)所示。Weigh 0.053g ZrCl 4 (0.227mmol), 0.034g terephthalic acid (0.227mmol) and 0.530g benzoic acid (4.344mmol) and join in 25ml of N,N-dimethylformamide, then sonicate after 30min It was transferred to a 30ml polytetrafluoroethylene reactor and reacted at 120°C for 24h. After the reaction, it was cooled to room temperature, filtered and washed several times with DMF and CHCl 3 , and dried under reduced pressure to obtain UiO-66. The XRD pattern of the obtained UiO-66 is shown in Figure 1, and the TEM image is shown in Figure 2(a).
为探索N-K2Ti4O9/g-C3N4/UiO-66降解有机污染物的应用,同时对比N-K2Ti4O9、g-C3N4、UiO-66、N-K2Ti4O9/g-C3N4二元复合材料和N-K2Ti4O9/g-C3N4/UiO-66作为催化剂时的光催化性能,作如下测试:取各催化剂20mg,加入到100mL 10mg/L的罗丹明B水溶液中,暗处吸附12h达到平衡,然后开启光源进行光催化实验,整个实验通过鼓气使催化剂和溶液混合均匀,使用循环冷却水维持反应器温度恒定。取样后,通过0.22μm过滤器进行过滤,吸光度在Shimadzu UV 2550紫外可见分光光度计上测定。结果如图3所示,二元N-K2Ti4O9/g-C3N4复合材料比纯材料的光催化性能好,三元N-K2Ti4O9/g-C3N4/UiO-66复合材料的光催化效果最好。In order to explore the application of NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 to degrade organic pollutants, and compare NK 2 Ti 4 O 9 , gC 3 N 4 , UiO-66, NK 2 Ti 4 O 9 /gC The photocatalytic performance of 3 N 4 binary composites and NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 as catalysts was tested as follows: 20 mg of each catalyst was added to 100 mL of 10 mg/L Rhodamine B In the aqueous solution, the dark place was adsorbed for 12 hours to reach equilibrium, and then the light source was turned on for the photocatalytic experiment. The catalyst and the solution were mixed evenly by blowing air throughout the experiment, and the temperature of the reactor was kept constant by using circulating cooling water. After sampling, it was filtered through a 0.22 μm filter, and the absorbance was measured on a Shimadzu UV 2550 UV-Vis spectrophotometer. The results are shown in Figure 3. The binary NK 2 Ti 4 O 9 /gC 3 N 4 composite has better photocatalytic performance than the pure material, and the ternary NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 composite the best photocatalytic effect.
实施例2Example 2
本实施例按实施例1相同的方式制备N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂,区别仅在于步骤6中N-K2Ti4O9/g-C3N4二元复合材料的质量改为0.027g。所得产物N-K2Ti4O9/g-C3N4/UiO-66(1:2)光催化性能如图4所示。In this example, NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst was prepared in the same manner as in Example 1, the only difference being that in step 6, NK 2 Ti 4 O 9 /gC 3 N 4 The mass of the binary composite is changed to 0.027g. The photocatalytic performance of the obtained product NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 (1:2) is shown in Fig. 4 .
实施例3Example 3
本实施例按实施例1相同的方式制备N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂,区别仅在于步骤6中N-K2Ti4O9/g-C3N4二元复合材料的质量改为0.035g。所得产物N-K2Ti4O9/g-C3N4/UiO-66(2:3)光催化性能如图所4示。In this example, NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst was prepared in the same manner as in Example 1, the only difference being that in step 6, NK 2 Ti 4 O 9 /gC 3 N 4 The mass of the binary composite is changed to 0.035g. The photocatalytic performance of the obtained product NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 (2:3) is shown in Figure 4 .
实施例4Example 4
本实施例按实施例1相同的方式制备N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂,区别仅在于步骤6中N-K2Ti4O9/g-C3N4二元复合材料的质量改为0.053g。所得产物N-K2Ti4O9/g-C3N4/UiO-66(1:1)光催化性能如图所4示。In this example, NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst was prepared in the same manner as in Example 1, the only difference being that in step 6, NK 2 Ti 4 O 9 /gC 3 N 4 The mass of the binary composite is changed to 0.053g. The photocatalytic performance of the obtained product NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 (1:1) is shown in Figure 4.
实施例5Example 5
本实施例按实施例1相同的方式制备N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂,区别仅在于步骤6中N-K2Ti4O9/g-C3N4二元复合材料的质量改为0.106g。所得产物N-K2Ti4O9/g-C3N4/UiO-66(2:1)光催化性能如图所4示。In this example, NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light photocatalyst was prepared in the same manner as in Example 1, the only difference being that in step 6, NK 2 Ti 4 O 9 /gC 3 N 4 The mass of the binary composite is changed to 0.106g. The photocatalytic performance of the obtained product NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 (2:1) is shown in Figure 4 .
对比实施例1~5可知将N-K2Ti4O9/g-C3N4和ZrCl4按照不同质量比制备出的N-K2Ti4O9/g-C3N4/UiO-66三元高效复合可见光光催化剂都具有较好的光催化性能,同时当N-K2Ti4O9/g-C3N4和ZrCl4的质量比为3:2时复合材料光催化性能最好。Comparing Examples 1 to 5, it can be seen that NK 2 Ti 4 O 9 /gC 3 N 4 /UiO-66 ternary high-efficiency composite visible light is prepared by NK 2 Ti 4 O 9 /gC 3 N 4 and ZrCl 4 according to different mass ratios. The catalysts all have good photocatalytic performance, and the photocatalytic performance of the composite material is the best when the mass ratio of NK 2 Ti 4 O 9 /gC 3 N 4 and ZrCl 4 is 3:2.
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Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103316714A (en) * | 2013-06-28 | 2013-09-25 | 中国石油大学(北京) | Catalyst for photo-catalytically decomposing water to produce hydrogen and preparation method of catalyst |
CN104128603A (en) * | 2014-08-13 | 2014-11-05 | 厦门大学 | Metal nanoparticle wrapped by zirconium-based porous shell and preparing method of metal nanoparticle |
CN104437645A (en) * | 2014-11-19 | 2015-03-25 | 河南工业大学 | Metal-organic framework supported heteropoly acid catalyst for synthesizing glutaraldehyde and production method of metal-organic framework supported heteropoly acid catalyst |
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Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103316714A (en) * | 2013-06-28 | 2013-09-25 | 中国石油大学(北京) | Catalyst for photo-catalytically decomposing water to produce hydrogen and preparation method of catalyst |
CN104128603A (en) * | 2014-08-13 | 2014-11-05 | 厦门大学 | Metal nanoparticle wrapped by zirconium-based porous shell and preparing method of metal nanoparticle |
CN104437645A (en) * | 2014-11-19 | 2015-03-25 | 河南工业大学 | Metal-organic framework supported heteropoly acid catalyst for synthesizing glutaraldehyde and production method of metal-organic framework supported heteropoly acid catalyst |
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Publication number | Priority date | Publication date | Assignee | Title |
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