CN108940304A - A kind of Mn/Ce/Cu base low-temperature plasma body catalyst and preparation and application - Google Patents
A kind of Mn/Ce/Cu base low-temperature plasma body catalyst and preparation and application Download PDFInfo
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- 239000003054 catalyst Substances 0.000 title claims abstract description 50
- 238000002360 preparation method Methods 0.000 title claims abstract description 15
- 239000010949 copper Substances 0.000 claims abstract description 46
- 239000011572 manganese Substances 0.000 claims abstract description 45
- 229910052751 metal Inorganic materials 0.000 claims abstract description 27
- 239000002184 metal Substances 0.000 claims abstract description 27
- 150000003839 salts Chemical class 0.000 claims abstract description 21
- 230000003197 catalytic effect Effects 0.000 claims abstract description 17
- 239000013078 crystal Substances 0.000 claims abstract description 15
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical class [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 claims abstract description 13
- 229910052802 copper Inorganic materials 0.000 claims abstract description 12
- 239000011259 mixed solution Substances 0.000 claims abstract description 11
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims abstract description 10
- 239000013110 organic ligand Substances 0.000 claims abstract description 8
- 230000004913 activation Effects 0.000 claims abstract description 5
- 238000002156 mixing Methods 0.000 claims abstract description 3
- 239000012265 solid product Substances 0.000 claims abstract description 3
- 239000012855 volatile organic compound Substances 0.000 claims description 18
- 238000000034 method Methods 0.000 claims description 15
- 229910052748 manganese Inorganic materials 0.000 claims description 12
- BDAGIHXWWSANSR-UHFFFAOYSA-N methanoic acid Natural products OC=O BDAGIHXWWSANSR-UHFFFAOYSA-N 0.000 claims description 12
- 230000003647 oxidation Effects 0.000 claims description 12
- 238000007254 oxidation reaction Methods 0.000 claims description 12
- 229910052684 Cerium Inorganic materials 0.000 claims description 8
- GWXLDORMOJMVQZ-UHFFFAOYSA-N cerium Chemical compound [Ce] GWXLDORMOJMVQZ-UHFFFAOYSA-N 0.000 claims description 8
- OSWFIVFLDKOXQC-UHFFFAOYSA-N 4-(3-methoxyphenyl)aniline Chemical compound COC1=CC=CC(C=2C=CC(N)=CC=2)=C1 OSWFIVFLDKOXQC-UHFFFAOYSA-N 0.000 claims description 6
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims description 6
- 235000019253 formic acid Nutrition 0.000 claims description 6
- 238000006731 degradation reaction Methods 0.000 claims description 5
- 230000015556 catabolic process Effects 0.000 claims description 4
- 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 claims description 4
- VGBWDOLBWVJTRZ-UHFFFAOYSA-K cerium(3+);triacetate Chemical compound [Ce+3].CC([O-])=O.CC([O-])=O.CC([O-])=O VGBWDOLBWVJTRZ-UHFFFAOYSA-K 0.000 claims description 2
- GHLITDDQOMIBFS-UHFFFAOYSA-H cerium(3+);tricarbonate Chemical compound [Ce+3].[Ce+3].[O-]C([O-])=O.[O-]C([O-])=O.[O-]C([O-])=O GHLITDDQOMIBFS-UHFFFAOYSA-H 0.000 claims description 2
- OZECDDHOAMNMQI-UHFFFAOYSA-H cerium(3+);trisulfate Chemical compound [Ce+3].[Ce+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O OZECDDHOAMNMQI-UHFFFAOYSA-H 0.000 claims description 2
- 229910000365 copper sulfate Inorganic materials 0.000 claims description 2
- XTVVROIMIGLXTD-UHFFFAOYSA-N copper(II) nitrate Chemical compound [Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XTVVROIMIGLXTD-UHFFFAOYSA-N 0.000 claims description 2
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical compound [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 claims description 2
- 229940071125 manganese acetate Drugs 0.000 claims description 2
- 235000006748 manganese carbonate Nutrition 0.000 claims description 2
- 239000011656 manganese carbonate Substances 0.000 claims description 2
- 229940093474 manganese carbonate Drugs 0.000 claims description 2
- 229940099596 manganese sulfate Drugs 0.000 claims description 2
- 235000007079 manganese sulphate Nutrition 0.000 claims description 2
- 239000011702 manganese sulphate Substances 0.000 claims description 2
- UOGMEBQRZBEZQT-UHFFFAOYSA-L manganese(2+);diacetate Chemical compound [Mn+2].CC([O-])=O.CC([O-])=O UOGMEBQRZBEZQT-UHFFFAOYSA-L 0.000 claims description 2
- MIVBAHRSNUNMPP-UHFFFAOYSA-N manganese(2+);dinitrate Chemical compound [Mn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MIVBAHRSNUNMPP-UHFFFAOYSA-N 0.000 claims description 2
- 229910000016 manganese(II) carbonate Inorganic materials 0.000 claims description 2
- SQQMAOCOWKFBNP-UHFFFAOYSA-L manganese(II) sulfate Chemical compound [Mn+2].[O-]S([O-])(=O)=O SQQMAOCOWKFBNP-UHFFFAOYSA-L 0.000 claims description 2
- XMWCXZJXESXBBY-UHFFFAOYSA-L manganese(ii) carbonate Chemical compound [Mn+2].[O-]C([O-])=O XMWCXZJXESXBBY-UHFFFAOYSA-L 0.000 claims description 2
- 230000035484 reaction time Effects 0.000 claims description 2
- 239000000463 material Substances 0.000 abstract description 21
- 239000012621 metal-organic framework Substances 0.000 abstract description 6
- 238000001354 calcination Methods 0.000 abstract description 4
- 238000006555 catalytic reaction Methods 0.000 abstract description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 2
- 229910052799 carbon Inorganic materials 0.000 abstract description 2
- 239000000470 constituent Substances 0.000 abstract 2
- 239000006185 dispersion Substances 0.000 abstract 1
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 42
- 238000006243 chemical reaction Methods 0.000 description 8
- 238000005516 engineering process Methods 0.000 description 7
- 238000010586 diagram Methods 0.000 description 4
- 239000000243 solution Substances 0.000 description 4
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 3
- 239000007864 aqueous solution Substances 0.000 description 3
- 239000006227 byproduct Substances 0.000 description 3
- 239000013084 copper-based metal-organic framework Substances 0.000 description 3
- 239000006228 supernatant Substances 0.000 description 3
- 229910002492 Ce(NO3)3·6H2O Inorganic materials 0.000 description 2
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 2
- 238000002441 X-ray diffraction Methods 0.000 description 2
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- 239000013177 MIL-101 Substances 0.000 description 1
- 206010028980 Neoplasm Diseases 0.000 description 1
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- 150000001299 aldehydes Chemical class 0.000 description 1
- 150000001335 aliphatic alkanes Chemical class 0.000 description 1
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- 150000001491 aromatic compounds Chemical class 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
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- 238000010000 carbonizing Methods 0.000 description 1
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- 150000002148 esters Chemical class 0.000 description 1
- -1 from pharmaceutical Chemical class 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 150000008282 halocarbons Chemical class 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 1
- 150000002576 ketones Chemical class 0.000 description 1
- 229910052746 lanthanum Inorganic materials 0.000 description 1
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- 229910052758 niobium Inorganic materials 0.000 description 1
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- 238000007639 printing Methods 0.000 description 1
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- 238000012360 testing method Methods 0.000 description 1
- 229910052723 transition metal Inorganic materials 0.000 description 1
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/76—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/84—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/889—Manganese, technetium or rhenium
- B01J23/8892—Manganese
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8678—Removing components of undefined structure
- B01D53/8687—Organic components
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/70—Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
- B01D2257/708—Volatile organic compounds V.O.C.'s
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2259/00—Type of treatment
- B01D2259/80—Employing electric, magnetic, electromagnetic or wave energy, or particle radiation
- B01D2259/818—Employing electrical discharges or the generation of a plasma
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Abstract
Description
技术领域technical field
本发明属于催化材料技术领域,具体涉及一种Mn/Ce/Cu基低温等离子体催化剂及制备与应用。The invention belongs to the technical field of catalytic materials, and in particular relates to a Mn/Ce/Cu-based low-temperature plasma catalyst and its preparation and application.
背景技术Background technique
挥发性有机物(volatile organic compounds,VOCs)种类繁多,包括烷类、烯烃、卤代烃、酯类、醛类、酮类和芳香族化合物等,主要来源于医药、石油化工、印刷等行业。大部分VOCs是有毒的,在光照下会发生反应形成光化学烟雾,是臭氧污染和PM2.5的前体物之一,长期呆在含挥发性有机物的环境中会增加癌症等疾病的可能性。因此,开展工业挥发性有机物污染治理具有极其重要的应用价值。Volatile organic compounds (volatile organic compounds, VOCs) are various, including alkanes, olefins, halogenated hydrocarbons, esters, aldehydes, ketones and aromatic compounds, mainly from pharmaceutical, petrochemical, printing and other industries. Most VOCs are toxic and will react under light to form photochemical smog, which is one of the precursors of ozone pollution and PM2.5. Long-term stay in an environment containing volatile organic compounds will increase the possibility of diseases such as cancer. Therefore, it has extremely important application value to carry out industrial volatile organic compound pollution control.
为有效地治理有机废气中VOCs污染,国内外广泛采用的技术有催化燃烧法、吸附法、吸收法等,近年来研究的治理技术还有生物膜法、光催化氧化法、等离子体法等。在诸多VOCs治理技术中,低温等离子体在常温常压下就能够快速降解VOCs而备受关注。然而,单纯的低温等离子体技术耗能高、选择性低,部分VOCs在降解过程中会生产成有毒的副产物。为了克服这些不足,将低温等离子体与催化氧化技术耦合,即在等离子体的放电区域装填催化剂,在等离子体与催化剂协同作用下,其对VOCs有机污染物的催化氧化效率和选择性得到大大的提高。催化剂是低温等离子体催化氧化技术的核心,已报道的催化剂有过渡金属催化剂、贵金属催化剂等。例如,H.T.Quoc An等[An H T Q,Huu T P,Van T L,etal.Application of atmospheric non thermal plasma-catalysis hybrid system forair pollution control:Toluene removal[J].Catalysis Today,2011,176(1):474-477.]制备了含Ag、Au、Cu、Co、Mn、La和Nb等元素的系列催化剂,其中1%(质量分数)Au/Al2O3和Nb2O5催化剂,其对甲苯的转化率达到96%。黄海保等人[龙丽萍,赵建国,杨利娴等常温下MnO2/Al2O3催化剂催化臭氧氧化甲苯反应[J].催化学报,2011,32(6):904-916.]将TiO2/γ-/Al2O3/发泡镍与等离子体结合处理VOCs,提高产物的CO2选择性,但此催化剂容易因副产物的堆积而失活。吴军良等[吴军良,夏启斌,刘治猛,等.Mn、Fe和Cu氧化物在低温等离子体催化氧化甲苯体系中的活性比较[J].功能材料,2012,43(10):1332-1335.]将金属有机骨架材料MIL-101与等离子体结合处理甲苯,甲苯的转化率达到100%,CO2选择性达到70%,可以显著减少反应副产物。由于MOFs骨架本身具有相对较差的稳定性(包括热稳定性、化学稳定性等),所以其工业应用受到了极大的限制。In order to effectively control VOCs pollution in organic waste gas, the technologies widely used at home and abroad include catalytic combustion method, adsorption method, absorption method, etc. In recent years, the treatment technologies studied include biofilm method, photocatalytic oxidation method, plasma method, etc. Among many VOCs treatment technologies, low-temperature plasma can quickly degrade VOCs at room temperature and pressure, and has attracted much attention. However, pure low-temperature plasma technology has high energy consumption and low selectivity, and some VOCs will be produced into toxic by-products during the degradation process. In order to overcome these shortcomings, the low-temperature plasma is coupled with catalytic oxidation technology, that is, the catalyst is loaded in the discharge area of the plasma. Under the synergistic effect of the plasma and the catalyst, the catalytic oxidation efficiency and selectivity of VOCs organic pollutants are greatly improved. improve. Catalysts are the core of low-temperature plasma catalytic oxidation technology. The reported catalysts include transition metal catalysts and noble metal catalysts. For example, HTQuoc An et al [An HTQ, Huu TP, Van TL, et al. Application of atmospheric non thermal plasma-catalysis hybrid system for air pollution control: Toluene removal[J].Catalysis Today,2011,176(1):474-477 .] prepared a series of catalysts containing elements such as Ag, Au, Cu, Co, Mn, La and Nb, wherein 1% (mass fraction) Au/Al 2 O 3 and Nb 2 O 5 catalysts, the conversion rate of its toluene Reached 96%. Huang Haibao et al [Long Liping, Zhao Jianguo, Yang Lixian et al. MnO 2 /Al 2 O 3 Catalyzed Ozone Oxidation of Toluene at Room Temperature[J]. Acta Catalytica Sinica, 2011,32(6):904-916.] TiO 2 /γ-/Al 2 O 3 /foamed nickel combined with plasma to treat VOCs can improve the CO 2 selectivity of the product, but the catalyst is easily deactivated by the accumulation of by-products. Wu Junliang et al[Wu Junliang, Xia Qibin, Liu Zhimeng, et al.Comparison of the activity of Mn, Fe and Cu oxides in low temperature plasma catalytic oxidation of toluene[J]. Functional Materials, 2012,43(10):1332-1335. ] Combining metal-organic framework material MIL-101 with plasma to treat toluene, the conversion rate of toluene reaches 100%, and the CO2 selectivity reaches 70%, which can significantly reduce the reaction by-products. Due to the relatively poor stability (including thermal stability, chemical stability, etc.) of the MOFs framework itself, its industrial application is greatly limited.
发明内容Contents of the invention
针对以上现有技术存在的缺点和不足之处,本发明的首要目的在于提供一种Mn/Ce/Cu基低温等离子体催化剂的制备方法。In view of the above shortcomings and deficiencies in the prior art, the primary purpose of the present invention is to provide a method for preparing a Mn/Ce/Cu-based low-temperature plasma catalyst.
本发明的另一目的在于提供一种通过上述方法制备得到的Mn/Ce/Cu基低温等离子体催化剂。Another object of the present invention is to provide a Mn/Ce/Cu-based low-temperature plasma catalyst prepared by the above method.
本发明的再一目的在于提供上述Mn/Ce/Cu基低温等离子体催化剂在低温等离子体催化氧化降解VOCs中的应用。Another object of the present invention is to provide the application of the above-mentioned Mn/Ce/Cu-based low-temperature plasma catalyst in low-temperature plasma catalytic oxidation degradation of VOCs.
本发明的又一目的在于提供上述中的应用。Another object of the present invention is to provide the above-mentioned application.
本发明目的通过以下技术方案实现:The object of the invention is achieved through the following technical solutions:
一种Mn/Ce/Cu基低温等离子体催化剂的制备方法,包括如下制备步骤:A kind of preparation method of Mn/Ce/Cu base low-temperature plasma catalyst, comprises following preparation steps:
(1)将含锰金属盐、含铈金属盐和含铜金属盐溶于DMF中,加入有机配体超声混合均匀,得到混合溶液;(1) dissolving manganese-containing metal salts, cerium-containing metal salts and copper-containing metal salts in DMF, adding organic ligands and ultrasonically mixing to obtain a mixed solution;
(2)将步骤(1)所得混合溶液在80~120℃温度下进行反应,固体产物浸泡于DMF中进行活化,得活化晶体;(2) reacting the mixed solution obtained in step (1) at a temperature of 80-120° C., immersing the solid product in DMF for activation to obtain activated crystals;
(3)将步骤(2)所得活化晶体经洗涤、干燥,然后于300~400℃焙烧,得到Mn/Ce/Cu基低温等离子体催化剂。(3) The activated crystal obtained in the step (2) is washed, dried, and then calcined at 300-400° C. to obtain a Mn/Ce/Cu-based low-temperature plasma catalyst.
进一步地,步骤(1)中所述含锰金属盐选自硝酸锰、硫酸锰、碳酸锰、醋酸锰中的至少一种;所述含铈金属盐选自硝酸铈、硫酸铈、碳酸铈、醋酸铈中的至少一种;所述含铜金属盐选自硝酸铜、硫酸铜中的至少一种。Further, the manganese-containing metal salt in step (1) is selected from at least one of manganese nitrate, manganese sulfate, manganese carbonate, and manganese acetate; the cerium-containing metal salt is selected from cerium nitrate, cerium sulfate, cerium carbonate, At least one of cerium acetate; the copper-containing metal salt is selected from at least one of copper nitrate and copper sulfate.
进一步地,步骤(1)中所述含锰金属盐、含铈金属盐和含铜金属盐的用量按照锰元素、铈元素和铜元素的摩尔比为1:2:(1~2)。更优选为1:2:1、1:2:1.5或1:2:2。Further, the amount of the manganese-containing metal salt, cerium-containing metal salt and copper-containing metal salt in step (1) is 1:2:(1-2) according to the molar ratio of manganese element, cerium element and copper element. More preferably 1:2:1, 1:2:1.5 or 1:2:2.
进一步地,步骤(1)中所述有机配体选自甲酸或乙酸,更优选为甲酸。Further, the organic ligand in step (1) is selected from formic acid or acetic acid, more preferably formic acid.
进一步地,步骤(1)中所述有机配体的用量与含锰金属盐中的锰元素的摩尔比为1:(5.8~9);更优选为1:5.8、1:7.2或1:9。Further, the molar ratio of the amount of the organic ligand in step (1) to the manganese element in the manganese-containing metal salt is 1: (5.8-9); more preferably 1:5.8, 1:7.2 or 1:9 .
进一步地,步骤(2)中所述反应的时间为10~15h。Further, the reaction time in step (2) is 10-15 hours.
进一步地,步骤(2)中所述浸泡于DMF中进行活化的时间为12~24h。Further, the time for activating by immersing in DMF in step (2) is 12-24 hours.
进一步地,步骤(3)中所述焙烧是在空气气氛下进行焙烧,焙烧时间为2~3h。Further, the calcination in step (3) is carried out under an air atmosphere, and the calcination time is 2-3 hours.
一种Mn/Ce/Cu基低温等离子体催化剂,通过上述方法制备得到。A Mn/Ce/Cu-based low-temperature plasma catalyst is prepared by the above method.
上述Mn/Ce/Cu基低温等离子体催化剂在低温等离子体催化氧化降解VOCs中的应用。Application of the above-mentioned Mn/Ce/Cu-based low-temperature plasma catalyst in low-temperature plasma catalytic oxidation degradation of VOCs.
本发明的原理为:直接将MOFs材料在一定的空气气氛下高温煅烧,有机配体碳化,得到纳米多孔碳基催化材料。该方法制备的碳化MOFs基催化材料具有金属活性组分高度分散,结构稳定等优点,且可以有效避免金属活性组分团聚,其催化活性和稳定性明显提高,可作为一种新型的基于碳化Mn/Ce/Cu基MOF催化材料,应用到低温等离子体催化氧化VOCs系统中,可实现在常温常压条件下对VOCs的高效去除。The principle of the invention is: directly calcining the MOFs material at a high temperature under a certain air atmosphere, carbonizing the organic ligands, and obtaining the nanoporous carbon-based catalytic material. The carbonized MOFs-based catalytic material prepared by this method has the advantages of highly dispersed metal active components and stable structure, and can effectively avoid the agglomeration of metal active components, and its catalytic activity and stability are significantly improved. /Ce/Cu-based MOF catalytic material, applied to a low-temperature plasma catalytic oxidation VOCs system, can achieve efficient removal of VOCs under normal temperature and pressure conditions.
本发明的制备方法及所得到的产物具有如下优点及有益效果:The preparation method of the present invention and the resulting product have the following advantages and beneficial effects:
(1)与传统负载型催化剂相比,本发明的催化剂具有金属活性组分高度分散,孔隙率高、结构稳定的特点,可以有效避免金属活性组分团聚,使其对VOCs如甲苯具有高催化氧化活性;(1) Compared with traditional supported catalysts, the catalyst of the present invention has the characteristics of highly dispersed metal active components, high porosity and stable structure, which can effectively avoid the agglomeration of metal active components and make it highly catalytic to VOCs such as toluene Oxidation activity;
(2)本发明制备方法使用的原料便宜易得,制备方法简单,有利于工业化大规模应用;(2) The raw materials used in the preparation method of the present invention are cheap and easy to obtain, and the preparation method is simple, which is conducive to large-scale industrial application;
(3)与现有催化技术相比,本发明的催化剂与等离子体装置联用能在常温常压下快速催化氧化甲苯,甲苯的转化率能够达到100%,CO2选择性高达88%。(3) Compared with the existing catalytic technology, the combination of the catalyst of the present invention and the plasma device can rapidly catalyze the oxidation of toluene at normal temperature and pressure, the conversion rate of toluene can reach 100%, and the CO selectivity is as high as 88%.
附图说明Description of drawings
图1为本发明实施例1~3所得Mn/Ce/Cu基低温等离子体催化剂的XRD图。FIG. 1 is an XRD pattern of Mn/Ce/Cu-based low-temperature plasma catalysts obtained in Examples 1-3 of the present invention.
图2为本发明实施例1~3所得Mn/Ce/Cu基低温等离子体催化剂在不同等离子体能量密度下的甲苯转化率图。Fig. 2 is a diagram of toluene conversion rates of Mn/Ce/Cu-based low-temperature plasma catalysts obtained in Examples 1-3 of the present invention under different plasma energy densities.
图3为本发明实施例1~3所得Mn/Ce/Cu基低温等离子体催化剂在不同等离子体能量密度下的CO2选择性图。Fig. 3 is a CO 2 selectivity diagram of Mn/Ce/Cu-based low-temperature plasma catalysts obtained in Examples 1-3 of the present invention under different plasma energy densities.
具体实施方式Detailed ways
下面结合实施例及附图对本发明作进一步详细的描述,但本发明的实施方式不限于此。The present invention will be further described in detail below in conjunction with the embodiments and the accompanying drawings, but the embodiments of the present invention are not limited thereto.
实施例1Example 1
(1)将520μL的质量浓度为50%的Mn(NO3)2水溶液、1.94gCe(NO3)3·6H2O和0.54gCu(NO3)2·3H2O加入到80mLDMF中,加入1000μL甲酸,超声10min混合均匀,得到混合溶液;(1) Add 520 μL of 50% Mn(NO 3 ) 2 aqueous solution, 1.94 g of Ce(NO 3 ) 3 6H 2 O and 0.54 g of Cu(NO 3 ) 2 3H 2 O into 80 mL of DMF, and add 1000 μL Formic acid, ultrasonically mixed for 10 minutes to obtain a mixed solution;
(2)将混合溶液置于80℃烘箱反应10h,待溶液冷却后,去除上清液,加入新鲜DMF,室温浸泡活化12h,制得活化晶体材料(Mn/Ce/Cu-MOF);(2) Place the mixed solution in an oven at 80°C for 10 hours. After the solution is cooled, remove the supernatant, add fresh DMF, soak and activate at room temperature for 12 hours, and obtain an activated crystal material (Mn/Ce/Cu-MOF);
(3)将活化晶体材料用DMF洗涤,过滤,把过滤后的材料放入50℃真空烘箱内烘干;将烘干之后的晶体材料放入马弗炉中300℃焙烧2h,制得Mn/Ce/Cu基低温等离子体催化剂。(3) The activated crystal material is washed with DMF, filtered, and the filtered material is dried in a vacuum oven at 50°C; the dried crystal material is put into a muffle furnace and roasted at 300°C for 2h to obtain Mn/ Ce/Cu based low temperature plasma catalyst.
实施例2Example 2
(1)将520μL的质量浓度为50%的Mn(NO3)2水溶液、1.94gCe(NO3)3·6H2O和0.81gCu(NO3)2·3H2O加入到80mLDMF中,加入1200μL甲酸,超声10min混合均匀,得到混合溶液;(1) Add 520 μL of 50% Mn(NO 3 ) 2 aqueous solution, 1.94 g of Ce(NO 3 ) 3 ·6H 2 O and 0.81 g of Cu(NO 3 ) 2 ·3H 2 O into 80 mL of DMF, and add 1200 μL Formic acid, ultrasonically mixed for 10 minutes to obtain a mixed solution;
(2)将混合溶液置于100℃烘箱反应12h,待溶液冷却后,去除上清液,加入新鲜DMF,室温浸泡活化18h,制得活化晶体材料(Mn/Ce/Cu-MOF);(2) Place the mixed solution in an oven at 100°C for 12 hours. After the solution is cooled, remove the supernatant, add fresh DMF, soak and activate at room temperature for 18 hours, and obtain an activated crystal material (Mn/Ce/Cu-MOF);
(3)将活化晶体材料用DMF洗涤,过滤,把过滤后的材料放入50℃真空烘箱内烘干;将烘干之后的晶体材料放入马弗炉中350℃焙烧2.5h,制得Mn/Ce/Cu基低温等离子体催化剂。(3) The activated crystal material is washed with DMF, filtered, and the filtered material is dried in a vacuum oven at 50°C; the dried crystal material is baked in a muffle furnace at 350°C for 2.5h to obtain Mn /Ce/Cu based low temperature plasma catalyst.
实施例3Example 3
(1)将520μL的质量浓度为50%的Mn(NO3)2水溶液、1.94gCe(NO3)3·6H2O和1.08gCu(NO3)2·3H2O加入到80mLDMF中,加入1500μL甲酸,超声10min混合均匀,得到混合溶液;(1) Add 520 μL of 50% Mn(NO 3 ) 2 aqueous solution, 1.94 g of Ce(NO 3 ) 3 ·6H 2 O and 1.08 g of Cu(NO 3 ) 2 ·3H 2 O into 80 mL of DMF, and add 1500 μL Formic acid, ultrasonically mixed for 10 minutes to obtain a mixed solution;
(2)将混合溶液置于120℃烘箱反应15h,待溶液冷却后,去除上清液,加入新鲜DMF,室温浸泡活化24h,制得活化晶体材料(Mn/Ce/Cu-MOF);(2) Place the mixed solution in an oven at 120°C for 15 hours. After the solution is cooled, remove the supernatant, add fresh DMF, soak and activate at room temperature for 24 hours, and obtain an activated crystal material (Mn/Ce/Cu-MOF);
(3)将活化晶体材料用DMF洗涤,过滤,把过滤后的材料放入50℃真空烘箱内烘干;将烘干之后的晶体材料放入马弗炉中400℃焙烧3h,制得Mn/Ce/Cu基低温等离子体催化剂。(3) The activated crystal material is washed with DMF, filtered, and the filtered material is dried in a vacuum oven at 50° C.; the dried crystal material is put into a muffle furnace and roasted at 400° C. for 3 hours to obtain Mn/ Ce/Cu based low temperature plasma catalyst.
以上实施例所得催化剂样品的表征及性能测定:The characterization and performance measurement of above embodiment gained catalyst sample:
(1)X射线衍射分析(1) X-ray diffraction analysis
采用德国Bruker公司D8-ADVANCE型X射线衍射仪,操作条件为铜靶,40KV,40mA,步长0.02度,扫描速度17.7秒/步。分别对实例1~3所制备的Mn/Ce/Cu基低温等离子体催化剂进行表征。A D8-ADVANCE X-ray diffractometer from German Bruker Company was adopted, and the operating conditions were copper target, 40KV, 40mA, step size 0.02 degrees, and scanning speed 17.7 seconds/step. The Mn/Ce/Cu-based low-temperature plasma catalysts prepared in Examples 1-3 were respectively characterized.
图1为本发明实施例1~3所制备的Mn/Ce/Cu基低温等离子体催化剂的XRD图谱。由图1可见,三种催化剂均具有相同的XRD谱图,特征峰位置相同,峰宽较宽,说明实施例1~3合成了目标催化剂。Fig. 1 is the XRD spectrum of the Mn/Ce/Cu-based low-temperature plasma catalyst prepared in Examples 1-3 of the present invention. It can be seen from Figure 1 that the three catalysts all have the same XRD spectrum, the characteristic peak positions are the same, and the peak width is wider, indicating that the target catalysts were synthesized in Examples 1-3.
(2)催化氧化性能测试(2) Catalytic oxidation performance test
分别取实施例1~3中所得Mn/Ce/Cu基低温等离子体催化剂,压面然后过40~60目筛,装填于扫描等离子体装置之中。活性测试条件如下:反应温度为35℃,反应压力为常压,气体总流量为100mL/min,甲苯浓度为30ppm,载气为干空气。甲苯浓度与CO2浓度通过气相色谱检测。The Mn/Ce/Cu-based low-temperature plasma catalysts obtained in Examples 1-3 were respectively taken, pressed on the surface, passed through a 40-60 mesh sieve, and loaded into a scanning plasma device. The activity test conditions are as follows: the reaction temperature is 35° C., the reaction pressure is normal pressure, the total gas flow rate is 100 mL/min, the toluene concentration is 30 ppm, and the carrier gas is dry air. Toluene concentration and CO2 concentration were detected by gas chromatography.
图2为本发明实施例1~3所得催化剂在不同等离子体能量密度下的甲苯转化率图。其中实施例2中的催化剂具有最好的甲苯降解能力,降解率在能量密度为294J/L时达到100%。Fig. 2 is a diagram of toluene conversion rates of the catalysts obtained in Examples 1-3 of the present invention under different plasma energy densities. The catalyst in Example 2 has the best ability to degrade toluene, and the degradation rate reaches 100% when the energy density is 294J/L.
图3为本发明实施例1~3所得催化剂在不同等离子体能量密度下的CO2选择性图。从图中可以看出,随着能量密度的增加,CO2选择性随之增加,能量密度为294J/L时,实施例2中的催化剂具有最好的CO2选择性,其CO2选择性达到88%。Fig. 3 is a CO2 selectivity diagram of the catalysts obtained in Examples 1-3 of the present invention under different plasma energy densities. It can be seen from the figure that as the energy density increases, the CO2 selectivity increases. When the energy density is 294J/L, the catalyst in Example 2 has the best CO2 selectivity, and its CO2 selectivity Reached 88%.
上述实施例为本发明较佳的实施方式,但本发明的实施方式并不受上述实施例的限制,其它的任何未背离本发明的精神实质与原理下所作的改变、修饰、替代、组合、简化,均应为等效的置换方式,都包含在本发明的保护范围之内。The above-mentioned embodiment is a preferred embodiment of the present invention, but the embodiment of the present invention is not limited by the above-mentioned embodiment, and any other changes, modifications, substitutions, combinations, Simplifications should be equivalent replacement methods, and all are included in the protection scope of the present invention.
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