CN111573773B - Application of titanium-based coordination polymer in photocatalytic degradation of dye wastewater - Google Patents
Application of titanium-based coordination polymer in photocatalytic degradation of dye wastewater Download PDFInfo
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- 239000013256 coordination polymer Substances 0.000 title claims abstract description 48
- 229920001795 coordination polymer Polymers 0.000 title claims abstract description 48
- 239000010936 titanium Substances 0.000 title claims abstract description 48
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 title claims abstract description 45
- 229910052719 titanium Inorganic materials 0.000 title claims abstract description 45
- 238000013033 photocatalytic degradation reaction Methods 0.000 title claims abstract description 24
- 239000002351 wastewater Substances 0.000 title claims abstract description 23
- 239000000243 solution Substances 0.000 claims abstract description 21
- RBTBFTRPCNLSDE-UHFFFAOYSA-N 3,7-bis(dimethylamino)phenothiazin-5-ium Chemical compound C1=CC(N(C)C)=CC2=[S+]C3=CC(N(C)C)=CC=C3N=C21 RBTBFTRPCNLSDE-UHFFFAOYSA-N 0.000 claims abstract description 18
- 229960000907 methylthioninium chloride Drugs 0.000 claims abstract description 18
- 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 claims abstract description 18
- 239000007864 aqueous solution Substances 0.000 claims abstract description 17
- 229940043267 rhodamine b Drugs 0.000 claims abstract description 17
- STZCRXQWRGQSJD-GEEYTBSJSA-M methyl orange Chemical compound [Na+].C1=CC(N(C)C)=CC=C1\N=N\C1=CC=C(S([O-])(=O)=O)C=C1 STZCRXQWRGQSJD-GEEYTBSJSA-M 0.000 claims abstract description 15
- 229940012189 methyl orange Drugs 0.000 claims abstract description 15
- 239000000463 material Substances 0.000 claims abstract description 14
- 239000013078 crystal Substances 0.000 claims abstract description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 6
- 238000010521 absorption reaction Methods 0.000 claims description 20
- WEVYAHXRMPXWCK-UHFFFAOYSA-N Acetonitrile Chemical compound CC#N WEVYAHXRMPXWCK-UHFFFAOYSA-N 0.000 claims description 12
- 229910052724 xenon Inorganic materials 0.000 claims description 11
- FHNFHKCVQCLJFQ-UHFFFAOYSA-N xenon atom Chemical compound [Xe] FHNFHKCVQCLJFQ-UHFFFAOYSA-N 0.000 claims description 11
- TWBYWOBDOCUKOW-UHFFFAOYSA-N isonicotinic acid Chemical compound OC(=O)C1=CC=NC=C1 TWBYWOBDOCUKOW-UHFFFAOYSA-N 0.000 claims description 8
- 229910021589 Copper(I) bromide Inorganic materials 0.000 claims description 7
- KFZMGEQAYNKOFK-UHFFFAOYSA-N Isopropanol Chemical compound CC(C)O KFZMGEQAYNKOFK-UHFFFAOYSA-N 0.000 claims description 4
- 238000001816 cooling Methods 0.000 claims description 4
- NKNDPYCGAZPOFS-UHFFFAOYSA-M copper(i) bromide Chemical compound Br[Cu] NKNDPYCGAZPOFS-UHFFFAOYSA-M 0.000 claims description 4
- 238000001035 drying Methods 0.000 claims description 4
- 239000003446 ligand Substances 0.000 claims description 4
- 239000002904 solvent Substances 0.000 claims description 4
- VXUYXOFXAQZZMF-UHFFFAOYSA-N titanium(IV) isopropoxide Chemical compound CC(C)O[Ti](OC(C)C)(OC(C)C)OC(C)C VXUYXOFXAQZZMF-UHFFFAOYSA-N 0.000 claims description 4
- 238000006243 chemical reaction Methods 0.000 claims description 3
- 239000010919 dye waste Substances 0.000 claims description 2
- 229920000642 polymer Polymers 0.000 claims description 2
- 238000005406 washing Methods 0.000 claims description 2
- 150000001875 compounds Chemical class 0.000 claims 1
- 238000012360 testing method Methods 0.000 abstract description 18
- 230000015556 catabolic process Effects 0.000 abstract description 13
- 238000006731 degradation reaction Methods 0.000 abstract description 13
- 239000007857 degradation product Substances 0.000 abstract description 4
- 238000003911 water pollution Methods 0.000 abstract description 3
- 230000000593 degrading effect Effects 0.000 abstract 2
- 125000004122 cyclic group Chemical group 0.000 abstract 1
- 238000003756 stirring Methods 0.000 description 21
- 238000000862 absorption spectrum Methods 0.000 description 9
- 230000007423 decrease Effects 0.000 description 9
- 238000002474 experimental method Methods 0.000 description 9
- 238000005259 measurement Methods 0.000 description 9
- 230000035484 reaction time Effects 0.000 description 9
- 238000001179 sorption measurement Methods 0.000 description 9
- 230000001699 photocatalysis Effects 0.000 description 6
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 4
- 238000000034 method Methods 0.000 description 3
- 238000007146 photocatalysis Methods 0.000 description 3
- 238000011160 research Methods 0.000 description 3
- STZCRXQWRGQSJD-UHFFFAOYSA-M sodium;4-[[4-(dimethylamino)phenyl]diazenyl]benzenesulfonate Chemical compound [Na+].C1=CC(N(C)C)=CC=C1N=NC1=CC=C(S([O-])(=O)=O)C=C1 STZCRXQWRGQSJD-UHFFFAOYSA-M 0.000 description 3
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 description 3
- 238000010586 diagram Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000001782 photodegradation Methods 0.000 description 2
- 229910010413 TiO 2 Inorganic materials 0.000 description 1
- OMOVVBIIQSXZSZ-UHFFFAOYSA-N [6-(4-acetyloxy-5,9a-dimethyl-2,7-dioxo-4,5a,6,9-tetrahydro-3h-pyrano[3,4-b]oxepin-5-yl)-5-formyloxy-3-(furan-3-yl)-3a-methyl-7-methylidene-1a,2,3,4,5,6-hexahydroindeno[1,7a-b]oxiren-4-yl] 2-hydroxy-3-methylpentanoate Chemical compound CC12C(OC(=O)C(O)C(C)CC)C(OC=O)C(C3(C)C(CC(=O)OC4(C)COC(=O)CC43)OC(C)=O)C(=C)C32OC3CC1C=1C=COC=1 OMOVVBIIQSXZSZ-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 230000005923 long-lasting effect Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- SOQBVABWOPYFQZ-UHFFFAOYSA-N oxygen(2-);titanium(4+) Chemical compound [O-2].[O-2].[Ti+4] SOQBVABWOPYFQZ-UHFFFAOYSA-N 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 239000011941 photocatalyst Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000005215 recombination Methods 0.000 description 1
- 230000006798 recombination Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000004753 textile Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J31/00—Catalysts comprising hydrides, coordination complexes or organic compounds
- B01J31/16—Catalysts comprising hydrides, coordination complexes or organic compounds containing coordination complexes
- B01J31/1691—Coordination polymers, e.g. metal-organic frameworks [MOF]
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01J35/00—Catalysts, in general, characterised by their form or physical properties
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- B01J35/39—Photocatalytic properties
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- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/308—Dyes; Colorants; Fluorescent agents
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/10—Photocatalysts
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Abstract
Description
技术领域technical field
本发明属于晶体材料应用技术领域,具体涉及一种钛基配位聚合物在光催化降解染料废水中的应用。The invention belongs to the technical field of crystal material application, in particular to the application of a titanium-based coordination polymer in photocatalytic degradation of dye wastewater.
背景技术Background technique
随着我国经济建设的快速发展,生产制造业所产生的废水逐年增加,由此造成的水环境污染问题日趋严重。其中纺织污染是造成水环境污染重要元凶之一,染料废水具有成分复杂、色度深、水质变化大、可生化性差等特点,是较难处理的废水之一。光催化技术能够利用光能氧化分解有机污染物,是治理各种染料废水的重要方法。纳米二氧化钛(TiO2)材料由于其低成本、高效能以及环境友好等特征被认为是最具潜能的光催化剂之一。然而,该类TiO2材料也存在一些不容忽视缺点,如能量带隙较宽、光生电子-空穴对复合速率较快及光生载流子寿命较短等,这些因素严重限制了其在光催化领域的实际应用。With the rapid development of my country's economic construction, the waste water produced by the manufacturing industry has increased year by year, and the resulting water environment pollution problem has become increasingly serious. Among them, textile pollution is one of the important culprits of water pollution. Dye wastewater has the characteristics of complex composition, deep chroma, large changes in water quality, and poor biodegradability. It is one of the more difficult wastewaters to treat. Photocatalysis technology can use light energy to oxidize and decompose organic pollutants, and it is an important method to treat various dye wastewater. Nano-titanium dioxide (TiO 2 ) is considered to be one of the most promising photocatalysts due to its low cost, high efficiency and environmental friendliness. However, this type of TiO2 material also has some shortcomings that cannot be ignored, such as wide energy band gap, fast photogenerated electron-hole pair recombination rate, and short photogenerated carrier lifetime, etc. These factors seriously limit its use in photocatalysis. practical applications in the field.
钛基配位聚合物因其在光催化方面的应用前景,成为了迄今为止报道的最具吸引力的配位聚合物之一。与半导体TiO2光催化材料相比,钛基配位聚合物具有诸多优势,如精确的原子层面结构信息、明确的配体-簇核连接方式、可调控的拓扑结构及易于修饰等。然而,钛基配位聚合物的研究一直处于初始阶段,对于其在染料废水处理方面的应用研究更少。有鉴于此,将钛基配位聚合物用于光催化降解染料废水就成为了重要研究课题。Titanium-based coordination polymers have become one of the most attractive coordination polymers reported so far due to their promising application in photocatalysis. Compared with semiconducting TiO photocatalytic materials, titanium-based coordination polymers have many advantages, such as precise atomic-level structural information, well-defined ligand-cluster-nucleus connection, tunable topology, and ease of modification. However, the research on titanium-based coordination polymers has been in its infancy, and less research has been done on its application in dye wastewater treatment. In view of this, the use of titanium-based coordination polymers for photocatalytic degradation of dye wastewater has become an important research topic.
发明内容SUMMARY OF THE INVENTION
为克服现有技术的缺陷,本发明提供了一种钛基配位聚合物在光催化降解染料废水中的应用,所述钛基配位聚合物材料在光降解染料废水降解测试显示出降解效率高、降解产物彻底、无二次污染、可循环利用等特点。In order to overcome the defects of the prior art, the present invention provides an application of a titanium-based coordination polymer in photocatalytic degradation of dye wastewater, and the titanium-based coordination polymer material shows degradation efficiency in the photodegradation dye wastewater degradation test. High, complete degradation products, no secondary pollution, recyclable and other characteristics.
为实现上述目的,本发明采取的技术方案为:To achieve the above object, the technical scheme adopted in the present invention is:
一种钛基配位聚合物在光催化降解染料废水中的应用,其特征在于,所述钛基配位聚合物材料对亚甲基蓝、罗丹明B、甲基橙水溶液进行降解。The application of a titanium-based coordination polymer in photocatalytic degradation of dye wastewater is characterized in that the titanium-based coordination polymer material degrades methylene blue, rhodamine B and methyl orange aqueous solutions.
进一步地,所述的光催化降解染料废水,采用以下步骤:将钛基配位聚合物分散在染料水溶液中,并将其置于配有滤光片(>420nm)的300W氙灯下进行光照,连续搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪对溶液进行分析。Further, the photocatalytic degradation of dye waste water adopts the following steps: dispersing the titanium-based coordination polymer in the dye aqueous solution, and placing it under a 300W xenon lamp equipped with a filter (>420nm) for illumination, With continuous stirring, 2 mL of the solution was taken out every 2 min, filtered, and the solution was analyzed by an ultraviolet absorption spectrometer.
进一步地,所述的加入的钛基配位聚合物和染料废水中亚甲基蓝物质的量的比为:1:(2~4);所述加入的钛基配位聚合物和染料废水中罗丹明B物质的量的比为:1:(2~4);所述加入的钛基配位聚合物和染料废水中甲基橙物质的量的比为:1:(2~4)。Further, the ratio of the amount of the added titanium-based coordination polymer and the amount of methylene blue substances in the dye wastewater is: 1: (2~4); the added titanium-based coordination polymer and the rhodamine in the dye wastewater are: The ratio of the amount of substance B is: 1: (2~4); the ratio of the amount of the added titanium-based coordination polymer and the amount of methyl orange in the dye wastewater is: 1: (2~4).
一种钛氧簇基配位聚合物的分子式为Ti3O12C30N3H47CuBr。The molecular formula of a titanium oxide cluster coordination polymer is Ti 3 O 12 C 30 N 3 H 47 CuBr.
进一步地,所述钛基配位聚合物的晶体结构为:晶体属于单斜晶系,空间群为C2/ c,晶胞参数为a=17.3730Å,b=19.2330Å,c=18.5000Å,α=90°,β=109°,γ=90°。Further, the crystal structure of the titanium-based coordination polymer is: the crystal belongs to the monoclinic system, the space group is C2/ c , the unit cell parameters are a=17.3730Å, b=19.2330Å, c=18.5000Å, α =90°, β=109°, γ=90°.
进一步地,钛基配位聚合物采用以下步骤合成:将钛酸异丙酯、溴化亚铜、异烟酸配体和乙腈溶剂加入反应釜中,室温下搅拌0.5~1.5h,于80~120℃中反应48~96h,降温至25℃,体系中析出块状晶体,分离、洗涤、干燥得到所的述钛基配位聚合物。Further, the titanium-based coordination polymer was synthesized by the following steps: adding isopropyl titanate, cuprous bromide, isonicotinic acid ligand and acetonitrile solvent into the reaction kettle, stirring at room temperature for 0.5-1.5 h, and stirring at room temperature for 80-10 h. The reaction was carried out at 120° C. for 48-96 hours, and the temperature was lowered to 25° C. to precipitate massive crystals in the system, which were separated, washed and dried to obtain the titanium-based coordination polymer.
进一步地,所述的钛酸异丙酯、溴化亚铜、异烟酸配体和乙腈溶剂的质量体积比为:(0.1~0.2)mL:(0.15~0.20)g:0.1g:(4~6)mL。Further, the mass-volume ratio of the isopropyl titanate, cuprous bromide, isonicotinic acid ligand and acetonitrile solvent is: (0.1~0.2) mL: (0.15~0.20) g: 0.1 g: (4 ~6) mL.
进一步地,所述降温采用程序控温的方式进行,降温速率控制在3~10℃/h;所述洗涤为采用异丙醇洗涤三次;所述的干燥为自然干燥。Further, the cooling is carried out by means of programmed temperature control, and the cooling rate is controlled at 3-10° C./h; the washing is three times with isopropanol; and the drying is natural drying.
有益效果beneficial effect
本发明提供了一种钛基配位聚合物在光催化降解染料废水中的应用,所述钛基配位聚合物材料在染料废水降解测试中降解效率高、降解产物彻底、无二次污染、可循环利用的特点。The invention provides the application of a titanium-based coordination polymer in photocatalytic degradation of dye wastewater. The titanium-based coordination polymer material has high degradation efficiency, complete degradation products, no secondary pollution, Recyclable features.
附图说明Description of drawings
图1为钛基配位聚合物的结构图;Figure 1 is a structural diagram of a titanium-based coordination polymer;
图2为实施例1光催化降解亚甲基蓝测试图;Fig. 2 is embodiment 1 photocatalytic degradation methylene blue test chart;
图3为实施例2光催化降解罗丹明B测试图;Fig. 3 is embodiment 2 photocatalytic degradation Rhodamine B test chart;
图4为实施例3光催化降解甲基橙测试图;Fig. 4 is
图5为实施例1-3光催化降解亚甲基蓝、罗丹明B、甲基橙的循环测试图。Figure 5 is a cycle test diagram of photocatalytic degradation of methylene blue, rhodamine B and methyl orange in Examples 1-3.
具体实施方式Detailed ways
下面通过具体的实施方案叙述本发明。除非特别说明,本发明中所用的技术手段均为本领域技术人员所公知的方法。另外,实施方案应理解为说明性的,而非限制本发明的范围,本发明的实质和范围仅由权利要求书所限定。对于本领域技术人员而言,在不背离本发明实质和范围的前提下,对这些实施方案中的物料成分和用量进行的各种改变或改动也属于本发明的保护范围。本发明所用原料及试剂均有市售。The present invention is described below through specific embodiments. Unless otherwise specified, the technical means used in the present invention are methods known to those skilled in the art. In addition, the embodiments are to be understood as illustrative, rather than limiting, of the scope of the invention, the spirit and scope of the invention being limited only by the claims. For those skilled in the art, on the premise of not departing from the spirit and scope of the present invention, various changes or modifications to the material components and dosages in these embodiments also belong to the protection scope of the present invention. The raw materials and reagents used in the present invention are commercially available.
为了使本发明的目的及优点更加清楚明白,以下结合实施例对本发明进行进一步详细说明。In order to make the objects and advantages of the present invention more clear, the present invention will be further described in detail below with reference to the embodiments.
实施例1Example 1
将10mg钛基配位聚合物分散在100mL亚甲基蓝水溶液(2×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,8min亚甲基蓝溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of methylene blue aqueous solution (2×10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) for continuous irradiation And stirring, take out 2mL solution every 2min, filter, analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum decreases with the increase of the reaction time. There is no new absorption peak in the entire measurement band. The methylene blue solution is completely degraded in 8 minutes, and the three cycle experiments show good photocatalytic degradation performance.
实施例2Example 2
将10mg钛基配位聚合物分散在100mL罗丹明B水溶液(2×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,12min罗丹明B溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of Rhodamine B aqueous solution (2×10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) Continue to irradiate and stir, take out 2 mL of the solution every 2 min, filter, and analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum decreases with the increase of the reaction time. No new absorption peak appears in the entire measurement band. The Rhodamine B solution was completely degraded in 12 minutes. The three cycle experiments showed good photocatalytic degradation performance. .
实施例3Example 3
将10mg钛基配位聚合物分散在100mL甲基橙水溶液(2×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,8min甲基橙溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of methyl orange aqueous solution (2 × 10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) Continue to irradiate and stir, take out 2 mL of the solution every 2 min, filter, and analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum decreases with the increase of the reaction time. There is no new absorption peak in the entire measurement band. The methyl orange solution is completely degraded in 8 minutes. The three cycle experiments show good photocatalytic degradation performance. .
实施例4Example 4
将10mg钛基配位聚合物分散在100mL亚甲基蓝水溶液(3×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,16min亚甲基蓝溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of methylene blue aqueous solution (3×10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) for continuous irradiation And stirring, take out 2mL solution every 2min, filter, analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum curve gradually decreases with the increase of the reaction time. There is no new absorption peak in the entire measurement band. The methylene blue solution is completely degraded in 16 minutes, and the three cycle experiments show good photocatalytic degradation performance.
实施例5Example 5
将10mg钛基配位聚合物分散在100mL罗丹明B水溶液(3×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,25min罗丹明B溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of Rhodamine B aqueous solution (3×10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) Continue to irradiate and stir, take out 2 mL of the solution every 2 min, filter, and analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum curve gradually decreases with the increase of reaction time, and no new absorption peak appears in the entire measurement band. The 25min Rhodamine B solution is completely degraded, and the three cycle experiments show good photocatalytic degradation performance. .
实施例6Example 6
将10mg钛基配位聚合物分散在100mL甲基橙水溶液(3×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,17min甲基橙溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of the titanium-based coordination polymer in 100 mL of methyl orange aqueous solution (3×10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) Continue to irradiate and stir, take out 2 mL of the solution every 2 min, filter, and analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum decreases with the increase of the reaction time. There is no new absorption peak in the entire measurement band. The methyl orange solution is completely degraded in 17 minutes. The three cycle experiments show good photocatalytic degradation performance. .
实施例7Example 7
将10mg钛基配位聚合物分散在100mL亚甲基蓝水溶液(4×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,25min亚甲基蓝溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of methylene blue aqueous solution (4×10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) for continuous irradiation And stirring, take out 2mL solution every 2min, filter, analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum decreases gradually with the increase of the reaction time. There is no new absorption peak in the entire measurement band. The methylene blue solution is completely degraded in 25 minutes. The three cycle experiments show good photocatalytic degradation performance.
实施例8Example 8
将10mg钛基配位聚合物分散在100mL罗丹明B水溶液(4×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,38min罗丹明B溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of Rhodamine B aqueous solution (4×10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) Continue to irradiate and stir, take out 2 mL of the solution every 2 min, filter, and analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum decreases with the increase of the reaction time. There is no new absorption peak in the entire measurement band. The Rhodamine B solution is completely degraded in 38 minutes, and the three cycle experiments show good photocatalytic degradation performance. .
实施例9Example 9
将10mg钛基配位聚合物分散在100mL甲基橙水溶液(4×10-4mol/L)中,避光条件下连续搅拌2h达到吸附饱和,再将其置于300W氙灯(>420nm)下持续照射并搅拌,每隔2min取出2mL溶液,过滤,通过紫外吸收光谱仪进行分析。测试结果见图2,紫外吸收光谱曲线随着反应时间增加峰高逐渐降低,在整个测量波段未出现新吸收峰,27min甲基橙溶液被降解完全,三次循环实验均显示出良好光催化降解性能。Disperse 10 mg of titanium-based coordination polymer in 100 mL of methyl orange aqueous solution (4 × 10 -4 mol/L), stir continuously for 2 h in the dark to achieve adsorption saturation, and then place it under a 300W xenon lamp (>420 nm) Continue to irradiate and stir, take out 2 mL of the solution every 2 min, filter, and analyze by ultraviolet absorption spectrometer. The test results are shown in Figure 2. The peak height of the UV absorption spectrum decreases with the increase of the reaction time. There is no new absorption peak in the entire measurement band. The methyl orange solution is completely degraded in 27 minutes. The three cycle experiments show good photocatalytic degradation performance. .
上述实施例1-9用于光降解染料废水的钛基配位聚合物,所述钛氧簇基配位聚合物的分子式为Ti3O12C30N3H47CuBr;所述钛基配位聚合物的晶体结构为:晶体属于单斜晶系,空间群为C2/c晶胞参数为a=17.3730Å,b=19.2330Å,c=18.5000Å,α=90°,β=109°,γ=90°。The titanium-based coordination polymers of the above examples 1-9 used for photodegradation of dye wastewater, the molecular formula of the titanium oxide cluster-based coordination polymers is Ti 3 O 12 C 30 N 3 H 47 CuBr; The crystal structure of the position polymer is: the crystal belongs to the monoclinic system, the space group is C2/c , and the unit cell parameters are a=17.3730Å, b=19.2330Å, c=18.5000Å, α=90°, β=109°, γ=90°.
钛基配位聚合物材料用于光催化降解染料废水。测试结果显示:所述钛基配位聚合物材料对2×10-4mol/L的亚甲基蓝、罗丹明B、甲基橙水溶液进行降解,分别在8min、12min、8min降解率达到100%;对3×10-4mol/L的亚甲基蓝、罗丹明B、甲基橙水溶液进行降解,分别在16min、25min、17min降解率达到100%;对4×10-4mol/L的亚甲基蓝、罗丹明B、甲基橙水溶液进行降解,分别在25min、38min、27min降解率达到100%(图2,3,4),三次循环测试表明所述该光催化材料具有持久光催化活性和良好光稳定性(图5)。所述钛基配位聚合物材料在染料废水降解测试中降解效率高、降解产物彻底、无二次污染、可循环利用等特点,在水污染处理领域具有广阔应用前景。Titanium-based coordination polymer materials are used for photocatalytic degradation of dye wastewater. The test results show that the titanium-based coordination polymer materials can degrade 2×10 -4 mol/L methylene blue, rhodamine B and methyl orange aqueous solutions, and the degradation rates reach 100% at 8min, 12min, and 8min respectively; 3×10 -4 mol/L methylene blue, rhodamine B and methyl orange aqueous solutions were degraded, and the degradation rate reached 100% in 16min, 25min and 17min respectively; 4×10 -4 mol/L methylene blue, rhodamine B , methyl orange aqueous solution was degraded, and the degradation rate reached 100% at 25min, 38min, and 27min respectively (Figure 2, 3, 4). Three cycle tests showed that the photocatalytic material has long-lasting photocatalytic activity and good photostability ( Figure 5). The titanium-based coordination polymer material has the characteristics of high degradation efficiency, complete degradation products, no secondary pollution, recyclability and the like in the dye wastewater degradation test, and has broad application prospects in the field of water pollution treatment.
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