CN110841714A - Iron-cobalt bimetal-organic framework material based on 2, 5-dihydroxy terephthalic acid ligand and preparation method and application thereof - Google Patents
Iron-cobalt bimetal-organic framework material based on 2, 5-dihydroxy terephthalic acid ligand and preparation method and application thereof Download PDFInfo
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- OYFRNYNHAZOYNF-UHFFFAOYSA-N 2,5-dihydroxyterephthalic acid Chemical compound OC(=O)C1=CC(O)=C(C(O)=O)C=C1O OYFRNYNHAZOYNF-UHFFFAOYSA-N 0.000 title claims abstract description 138
- 239000000463 material Substances 0.000 title claims abstract description 81
- 239000013384 organic framework Substances 0.000 title claims abstract description 81
- QVYYOKWPCQYKEY-UHFFFAOYSA-N [Fe].[Co] Chemical compound [Fe].[Co] QVYYOKWPCQYKEY-UHFFFAOYSA-N 0.000 title claims abstract description 78
- 239000003446 ligand Substances 0.000 title claims abstract description 64
- 238000002360 preparation method Methods 0.000 title claims abstract description 19
- 238000006243 chemical reaction Methods 0.000 claims abstract description 40
- 238000011282 treatment Methods 0.000 claims abstract description 37
- 239000002351 wastewater Substances 0.000 claims abstract description 30
- FHHJDRFHHWUPDG-UHFFFAOYSA-L peroxysulfate(2-) Chemical compound [O-]OS([O-])(=O)=O FHHJDRFHHWUPDG-UHFFFAOYSA-L 0.000 claims abstract description 23
- 239000002243 precursor Substances 0.000 claims abstract description 17
- 239000002957 persistent organic pollutant Substances 0.000 claims abstract description 13
- 238000004065 wastewater treatment Methods 0.000 claims abstract description 13
- QGUAJWGNOXCYJF-UHFFFAOYSA-N cobalt dinitrate hexahydrate Chemical compound O.O.O.O.O.O.[Co+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O QGUAJWGNOXCYJF-UHFFFAOYSA-N 0.000 claims abstract description 8
- 230000001590 oxidative effect Effects 0.000 claims abstract description 7
- 229960002089 ferrous chloride Drugs 0.000 claims abstract description 6
- NMCUIPGRVMDVDB-UHFFFAOYSA-L iron dichloride Chemical compound Cl[Fe]Cl NMCUIPGRVMDVDB-UHFFFAOYSA-L 0.000 claims abstract description 6
- 239000003960 organic solvent Substances 0.000 claims abstract description 5
- 238000004729 solvothermal method Methods 0.000 claims abstract description 5
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical group CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 claims description 60
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 18
- OKBMCNHOEMXPTM-UHFFFAOYSA-M potassium peroxymonosulfate Chemical compound [K+].OOS([O-])(=O)=O OKBMCNHOEMXPTM-UHFFFAOYSA-M 0.000 claims description 11
- 239000002244 precipitate Substances 0.000 claims description 8
- 239000008367 deionised water Substances 0.000 claims description 6
- 229910021641 deionized water Inorganic materials 0.000 claims description 6
- 238000001035 drying Methods 0.000 claims description 6
- 239000003054 catalyst Substances 0.000 claims description 5
- -1 polytetrafluoroethylene Polymers 0.000 claims description 4
- 230000035484 reaction time Effects 0.000 claims description 4
- 238000003756 stirring Methods 0.000 claims description 4
- 238000005406 washing Methods 0.000 claims description 4
- 238000001816 cooling Methods 0.000 claims description 2
- YMGGAHMANIOXGP-UHFFFAOYSA-L disodium;oxido sulfate Chemical group [Na+].[Na+].[O-]OS([O-])(=O)=O YMGGAHMANIOXGP-UHFFFAOYSA-L 0.000 claims description 2
- WSSMOXHYUFMBLS-UHFFFAOYSA-L iron dichloride tetrahydrate Chemical compound O.O.O.O.[Cl-].[Cl-].[Fe+2] WSSMOXHYUFMBLS-UHFFFAOYSA-L 0.000 claims description 2
- 238000002156 mixing Methods 0.000 claims description 2
- 239000007800 oxidant agent Substances 0.000 claims description 2
- 239000002994 raw material Substances 0.000 claims description 2
- QAOWNCQODCNURD-UHFFFAOYSA-M hydrogensulfate Chemical compound OS([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-M 0.000 claims 1
- FHHJDRFHHWUPDG-UHFFFAOYSA-N peroxysulfuric acid Chemical compound OOS(O)(=O)=O FHHJDRFHHWUPDG-UHFFFAOYSA-N 0.000 claims 1
- 229920001343 polytetrafluoroethylene Polymers 0.000 claims 1
- 239000004810 polytetrafluoroethylene Substances 0.000 claims 1
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 abstract description 12
- 229910052742 iron Inorganic materials 0.000 abstract description 7
- 229910017052 cobalt Inorganic materials 0.000 abstract description 5
- 239000010941 cobalt Substances 0.000 abstract description 5
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 abstract description 5
- 230000007613 environmental effect Effects 0.000 abstract description 5
- 231100000331 toxic Toxicity 0.000 abstract description 5
- 230000002588 toxic effect Effects 0.000 abstract description 5
- 229910001429 cobalt ion Inorganic materials 0.000 abstract description 4
- XLJKHNWPARRRJB-UHFFFAOYSA-N cobalt(2+) Chemical compound [Co+2] XLJKHNWPARRRJB-UHFFFAOYSA-N 0.000 abstract description 3
- 150000002500 ions Chemical class 0.000 abstract description 2
- CXKWCBBOMKCUKX-UHFFFAOYSA-M methylene blue Chemical compound [Cl-].C1=CC(N(C)C)=CC2=[S+]C3=CC(N(C)C)=CC=C3N=C21 CXKWCBBOMKCUKX-UHFFFAOYSA-M 0.000 description 29
- 229960000907 methylthioninium chloride Drugs 0.000 description 29
- 230000000694 effects Effects 0.000 description 12
- 238000000034 method Methods 0.000 description 11
- 230000003647 oxidation Effects 0.000 description 9
- 238000007254 oxidation reaction Methods 0.000 description 9
- 239000000975 dye Substances 0.000 description 8
- XNGIFLGASWRNHJ-UHFFFAOYSA-N phthalic acid Chemical compound OC(=O)C1=CC=CC=C1C(O)=O XNGIFLGASWRNHJ-UHFFFAOYSA-N 0.000 description 8
- 230000015556 catabolic process Effects 0.000 description 7
- 238000006731 degradation reaction Methods 0.000 description 7
- 239000000203 mixture Substances 0.000 description 7
- 238000005516 engineering process Methods 0.000 description 6
- 238000001000 micrograph Methods 0.000 description 6
- 239000002638 heterogeneous catalyst Substances 0.000 description 5
- HDMGAZBPFLDBCX-UHFFFAOYSA-M potassium;sulfooxy sulfate Chemical compound [K+].OS(=O)(=O)OOS([O-])(=O)=O HDMGAZBPFLDBCX-UHFFFAOYSA-M 0.000 description 5
- 230000003197 catalytic effect Effects 0.000 description 4
- 239000013078 crystal Substances 0.000 description 4
- 239000003344 environmental pollutant Substances 0.000 description 4
- 239000012621 metal-organic framework Substances 0.000 description 4
- 231100000719 pollutant Toxicity 0.000 description 4
- QPCDCPDFJACHGM-UHFFFAOYSA-N N,N-bis{2-[bis(carboxymethyl)amino]ethyl}glycine Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(=O)O)CCN(CC(O)=O)CC(O)=O QPCDCPDFJACHGM-UHFFFAOYSA-N 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
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- 239000010815 organic waste Substances 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 238000001291 vacuum drying Methods 0.000 description 3
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 2
- ATHHXGZTWNVVOU-UHFFFAOYSA-N N-methylformamide Chemical compound CNC=O ATHHXGZTWNVVOU-UHFFFAOYSA-N 0.000 description 2
- 239000012425 OXONE® Substances 0.000 description 2
- 230000002378 acidificating effect Effects 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 238000002329 infrared spectrum Methods 0.000 description 2
- 230000007935 neutral effect Effects 0.000 description 2
- 125000005385 peroxodisulfate group Chemical group 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 229910052723 transition metal Inorganic materials 0.000 description 2
- 150000003624 transition metals Chemical class 0.000 description 2
- 238000003911 water pollution Methods 0.000 description 2
- JTNCEQNHURODLX-UHFFFAOYSA-N 2-phenylethanimidamide Chemical compound NC(=N)CC1=CC=CC=C1 JTNCEQNHURODLX-UHFFFAOYSA-N 0.000 description 1
- 229910017061 Fe Co Inorganic materials 0.000 description 1
- 206010049290 Feminisation acquired Diseases 0.000 description 1
- 208000034793 Feminization Diseases 0.000 description 1
- 206010028980 Neoplasm Diseases 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 201000011510 cancer Diseases 0.000 description 1
- 230000000711 cancerogenic effect Effects 0.000 description 1
- 231100000315 carcinogenic Toxicity 0.000 description 1
- 239000002537 cosmetic Substances 0.000 description 1
- 238000004042 decolorization Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000004043 dyeing Methods 0.000 description 1
- TUJKJAMUKRIRHC-UHFFFAOYSA-N hydroxyl Chemical compound [OH] TUJKJAMUKRIRHC-UHFFFAOYSA-N 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 238000001095 inductively coupled plasma mass spectrometry Methods 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000033116 oxidation-reduction process Effects 0.000 description 1
- 238000010525 oxidative degradation reaction Methods 0.000 description 1
- 230000000737 periodic effect Effects 0.000 description 1
- 229910000343 potassium bisulfate Inorganic materials 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 238000001338 self-assembly Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
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- 238000001179 sorption measurement Methods 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 230000003390 teratogenic effect Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 229910001428 transition metal ion Inorganic materials 0.000 description 1
- 239000003403 water pollutant Substances 0.000 description 1
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- 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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- B01J31/00—Catalysts comprising hydrides, coordination complexes or organic compounds
- B01J31/26—Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
- B01J31/28—Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of the platinum group metals, iron group metals or copper
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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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
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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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
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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
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Abstract
本发明涉及一种基于2,5‑二羟基对苯二甲酸配体的铁钴双金属‑有机骨架材料及其制备方法和应用,将六水合硝酸钴、四水合氯化亚铁和2,5‑二羟基对苯二甲酸溶于有机溶剂中得到前驱体溶液;将前驱体溶液在110~170℃下进行溶剂热反应;反应结束后经后处理得到铁钴双金属‑有机骨架材料。该铁钴双金属‑有机骨架材料中高度分散的钴和铁活性中心离子可增强钴离子和铁与过一硫酸氢盐的有效接触使其产生具有强氧化性的硫酸根自由基,从而将废水中的难降解有机污染物去除。本发明基于2,5‑二羟基对苯二甲酸配体的铁钴双金属‑有机骨架材料适用于各种有机废水处理,效率高、持久性好、操作方便、环境友好,为处理有毒有害难生物降解的有机废水提供了广阔的前景。
The present invention relates to an iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand and a preparation method and application thereof. Cobalt nitrate hexahydrate, ferrous chloride tetrahydrate and 2,5 -Dihydroxyterephthalic acid is dissolved in an organic solvent to obtain a precursor solution; the precursor solution is subjected to a solvothermal reaction at 110-170°C; after the reaction is completed, an iron-cobalt bimetal-organic framework material is obtained by post-treatment. The highly dispersed cobalt and iron active center ions in the iron-cobalt bimetallic-organic framework material can enhance the effective contact of cobalt ions and iron with peroxymonosulfate to generate sulfate radicals with strong oxidizing properties, thereby reducing waste water Removal of refractory organic pollutants. The iron-cobalt bimetal-organic framework material based on the 2,5-dihydroxyterephthalic acid ligand of the invention is suitable for various organic wastewater treatment, has high efficiency, good durability, convenient operation and environmental friendliness, and is difficult to deal with toxic and harmful. Biodegradable organic wastewater offers great prospects.
Description
技术领域technical field
本发明属于水污染控制技术领域,具体涉及一种基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料及其制备方法和应用。The invention belongs to the technical field of water pollution control, and in particular relates to an iron-cobalt bimetallic-organic framework material based on a 2,5-dihydroxyterephthalic acid ligand and a preparation method and application thereof.
背景技术Background technique
随着工业的迅猛发展,水污染环境的治理成为世界性难题,难降解有机污染物的广泛存在使得水治理越来越受到人们的关注。难降解有机污染物由于其成分复杂、结构稳定、半衰期长,用传统的生物、物理及化学方法难以去除。并且大部分难降解有机污染物具有一定的毒性,易于在生物体内滞留,从而导致人和动物癌变、畸变及雌性化等。高级氧化技术具有快速、无选择性、氧化彻底等特点,对环境中微量难降解有机污染物及高浓度有机废水等均有较好的处理效果,为解决这一环境问题提高了有效的解决途径。因此,高级氧化技术逐渐成为处理难降解有机污染物的首选方法。With the rapid development of industry, the treatment of water pollution environment has become a worldwide problem, and the widespread existence of refractory organic pollutants has made water treatment more and more people's attention. Refractory organic pollutants are difficult to remove by traditional biological, physical and chemical methods due to their complex composition, stable structure and long half-life. And most of the refractory organic pollutants have certain toxicity and are easy to be retained in the organism, resulting in cancer, distortion and feminization of humans and animals. Advanced oxidation technology has the characteristics of rapid, non-selective, and thorough oxidation, and has a good treatment effect on trace refractory organic pollutants and high-concentration organic wastewater in the environment, which improves an effective solution to this environmental problem. . Therefore, advanced oxidation technology has gradually become the preferred method for the treatment of refractory organic pollutants.
近年来基于SO4 -·的高级氧化技术因其氧化能力强、适用pH范围广、操作简单等优点引起了越来越多研究者的关注与研究。采用过渡金属活化PS产生自由基SO4 -·是最有效的方式。通过分解过硫酸盐(peroxysulphate,PS)产生氧化能力极强的SO4 -·。相对于羟基自由基(·OH),SO4 -·具有与其(·OH,E0=2.6vs.NHE)相当的氧化还原电位,E0=2.5~3.1vs.NHE,而且SO4 -·在中性条件下对有机废水具有更好的处理效果,这使得基于SO4 -·的高级氧化技术在水处理方面更突出。SO4 -·可以通过分解过二硫酸盐(PDS)和过一硫酸氢盐(PMS)产生。辐射、紫外光和高温等方法均可催化PMS产生SO4 -·,但因过渡金属催化方法不需要外加热源和光源,反应体系简单而得到了广泛的关注。金属有机骨架材料(Metal-Organic Framework,MOFs)是一类由无机金属节点和有机桥连配体通过配位自组装得到的具有周期性结构的新型材料。最近研究表明,MOFs作为多相催化剂在污染环境治理方面表现出了突出的性能,特别是在水体污染物的去除方面表现出巨大的应用前景。In recent years, advanced oxidation technology based on SO 4 -· has attracted more and more researchers' attention and research because of its strong oxidizing ability, wide applicable pH range and simple operation. Using transition metal to activate PS to generate radical SO 4 -· is the most effective way. SO 4 -· is produced by decomposing peroxysulphate (PS) with strong oxidizing ability. With respect to the hydroxyl radical (·OH), SO 4 −· has an oxidation-reduction potential equivalent to that of (·OH, E 0 =2.6vs.NHE), E 0 =2.5-3.1vs.NHE, and SO 4 −· in Under neutral conditions, it has better treatment effect on organic wastewater, which makes the advanced oxidation technology based on SO 4 -· more prominent in water treatment. SO4- · can be produced by decomposition of peroxodisulfate (PDS) and peroxymonosulfate (PMS). Radiation, ultraviolet light and high temperature can catalyze the production of SO 4 -· from PMS. However, the transition metal catalysis method does not require external heat source and light source, and the reaction system is simple and has received extensive attention. Metal-Organic Frameworks (MOFs) are a new class of materials with periodic structures obtained by self-assembly of inorganic metal nodes and organic bridging ligands through coordination. Recent studies have shown that MOFs as heterogeneous catalysts have shown outstanding performance in the treatment of polluted environments, especially in the removal of water pollutants, showing great application prospects.
发明内容SUMMARY OF THE INVENTION
为了克服现有技术中钴离子活化过一硫酸氢盐反应体系中存在的钴离子不能回收利用且对环境造成二次污染而需进一步增加离子交换、吸附、沉淀分离等处理工艺,增加了处理成本等问题和缺点,本发明提供了一种铁钴双金属-有机骨架材料及其制备方法和在废水处理领域中的应用。In order to overcome the fact that the cobalt ions in the cobalt ion-activated peroxymonosulfate reaction system in the prior art cannot be recycled and cause secondary pollution to the environment, it is necessary to further increase treatment processes such as ion exchange, adsorption, precipitation and separation, which increases the treatment cost. To solve the problems and disadvantages, the present invention provides an iron-cobalt bimetallic-organic framework material, a preparation method thereof, and an application in the field of wastewater treatment.
一种基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料(FeCo-DHTA),由下述原料组分制备而得:六水合硝酸钴、四水合氯化亚铁、2,5-二羟基对苯二甲酸,所述六水合硝酸钴、四水合氯化亚铁、2,5-二羟基对苯二甲酸的摩尔比4:1:2.5~1:4:2.5。An iron-cobalt bimetallic-organic framework material (FeCo-DHTA) based on 2,5-dihydroxyterephthalic acid ligand, prepared from the following raw material components: cobalt nitrate hexahydrate, chloride tetrahydrate Iron, 2,5-dihydroxyterephthalic acid, the molar ratio of the cobalt nitrate hexahydrate, ferrous chloride tetrahydrate, and 2,5-dihydroxyterephthalic acid is 4:1:2.5~1:4: 2.5.
作为优选,所述基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的形态为规则的中空的多面体或棒状结构。Preferably, the shape of the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand is a regular hollow polyhedron or rod-like structure.
本发明还提供了上述基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的制备方法,包括下述步骤:The present invention also provides the above-mentioned preparation method of the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand, comprising the following steps:
(1)前驱体溶液的制备:将六水合硝酸钴、四水合氯化亚铁和2,5-二羟基对苯二甲酸溶于有机溶剂中,然后混合均匀,得到前驱体溶液;(1) Preparation of precursor solution: dissolving cobalt nitrate hexahydrate, ferrous chloride tetrahydrate and 2,5-dihydroxyterephthalic acid in an organic solvent, and then mixing uniformly to obtain a precursor solution;
(2)基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的制备:将步骤(1)制得的前驱体溶液在110~170℃的温度下进行溶剂热反应;冷却,洗涤,干燥,得到基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料。(2) Preparation of iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand: the precursor solution obtained in step (1) is subjected to solvothermal treatment at a temperature of 110-170 °C reaction; cooling, washing, and drying to obtain an iron-cobalt bimetallic-organic framework material based on a 2,5-dihydroxyterephthalic acid ligand.
作为优选,所述有机溶剂为N,N-二甲基甲酰胺和无水乙醇,所述N,N-二甲基甲酰胺和无水乙醇的体积比为1:1或者1:0。可以有效减少N,N-二甲基甲酰胺的用量,提高环境友好性,另外,避免使用氢氟酸等有毒有害溶剂,操作更为简便,对环境更为友好。Preferably, the organic solvent is N,N-dimethylformamide and absolute ethanol, and the volume ratio of the N,N-dimethylformamide and absolute ethanol is 1:1 or 1:0. The dosage of N,N-dimethylformamide can be effectively reduced, and the environmental friendliness can be improved. In addition, the use of toxic and harmful solvents such as hydrofluoric acid is avoided, the operation is simpler and the environment is more friendly.
作为优选,所述溶剂热反应在聚四氟乙烯内衬的高压反应釜中进行,所述溶剂热反应时间为24~48h;所述洗涤条件为:采用无水乙醇、N,N-二甲基甲酰胺和去离子水交替反复洗涤沉淀物;所述干燥的条件为:60~100℃干燥12~24h。Preferably, the solvothermal reaction is carried out in a polytetrafluoroethylene-lined high-pressure reaction kettle, and the solvothermal reaction time is 24-48 h; the washing conditions are: using absolute ethanol, N,N-dimethylformaldehyde The precipitate is washed alternately and repeatedly with methylformamide and deionized water; the drying conditions are: drying at 60-100° C. for 12-24 hours.
另外,本发明还提供了上述所述基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料在废水处理领域中的应用。In addition, the present invention also provides the application of the above-mentioned iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand in the field of wastewater treatment.
作为优选,所述基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的应用,包括下述步骤:向废水中加入作为氧化剂的过一硫酸氢盐和作为催化剂的基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料,进行废水处理反应。本发明基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料可高效催化活化过一硫酸氢盐快速有效去除废水中有毒有害难生物降解有机物。Preferably, the application of the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligands includes the following steps: adding peroxymonosulfate as an oxidant and as a catalyst into the wastewater 2,5-dihydroxyterephthalic acid ligand-based iron-cobalt bimetallic-organic framework materials for wastewater treatment reactions. The iron-cobalt bimetallic-organic framework material based on the 2,5-dihydroxyterephthalic acid ligand of the invention can efficiently catalyze and activate peroxymonosulfate to rapidly and effectively remove toxic, harmful, and biodegradable organic substances in wastewater.
作为优选,所述过一硫酸氢盐为过一硫酸氢钠或过一硫酸氢钾。Preferably, the peroxymonosulfate is sodium peroxymonosulfate or potassium peroxymonosulfate.
作为优选,所述过一硫酸氢盐与废水的有机污染物的摩尔比为6~300:1,所述基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的投加量为20~200mg/L。过一硫酸氢盐的投加量根据废水的有机污染物浓度而定,有机污染物的浓度越大,投加的过一硫酸氢盐量就越多。Preferably, the molar ratio of the peroxymonosulfate to organic pollutants in the wastewater is 6-300:1, and the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligands The dosage is 20 ~ 200mg/L. The dosage of peroxymonosulfate is determined according to the concentration of organic pollutants in the wastewater. The greater the concentration of organic pollutants, the greater the amount of peroxymonosulfate added.
作为优选,废水处理反应的温度为20~60℃,时间为2~30min;废水处理反应在搅拌或震荡条件下进行,搅拌或震荡的转速为50~200rpm;所述废水为有机废水,所述有机废水的pH值为3.0~11.0。Preferably, the temperature of the wastewater treatment reaction is 20 to 60°C, and the time is 2 to 30 minutes; the wastewater treatment reaction is carried out under stirring or shaking conditions, and the stirring or shaking speed is 50 to 200 rpm; the wastewater is organic wastewater, and the The pH value of the organic wastewater is 3.0 to 11.0.
本发明的原理:本发明提出的利用基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料高效活化过一硫酸氢盐的水处理技术是将基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料作为过一硫酸氢盐的非均相催化剂,在基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料和过一硫酸氢盐同时存在下与待处理的有机废水反应,基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料中分散均匀的和铁离子和钴金属离子可以高效活化过一硫酸氢盐产生强氧化性的SO4 -·,进而可以达到高效去除难降解有机污染物的目的。该反应能在较宽pH值范围内进行,而且催化剂用量少,反应时间短,同时具有催化氧化速率高,设备简单、操作方便、环境友好、催化剂易于回收利用等优点,在废水的深度处理领域有很大的应用潜力。Principle of the present invention: The water treatment technology proposed by the present invention to efficiently activate peroxymonosulfate using iron-cobalt bimetallic-organic framework materials based on 2,5-dihydroxyterephthalic acid ligands is based on 2,5- Iron-Cobalt Bimetallic-Organic Frameworks with Dihydroxyterephthalic Acid Ligands as Heterogeneous Catalysts for Peroxymonosulfate Reacting with organic wastewater to be treated in the presence of framework material and peroxymonosulfate, the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligands is uniformly dispersed and iron ions and cobalt Metal ions can efficiently activate peroxymonosulfate to produce strongly oxidizing SO 4 -· , which can achieve the purpose of efficiently removing refractory organic pollutants. The reaction can be carried out in a wide pH range, and the catalyst dosage is small, the reaction time is short, and the catalytic oxidation rate is high, the equipment is simple, the operation is convenient, the environment is friendly, and the catalyst is easy to recycle. The field has great application potential.
本发明相对于现有技术具有有益效果在于:Compared with the prior art, the present invention has beneficial effects as follows:
(1)本发明提供的铁钴双金属-有机骨架材料制备方法简单,反应条件温和,对外界环境条件无特殊要求,操作简单,重复操作性强,易于实现;(1) The preparation method of the iron-cobalt bimetallic-organic framework material provided by the present invention is simple, the reaction conditions are mild, there is no special requirement for external environmental conditions, the operation is simple, the repeatability is strong, and it is easy to realize;
(2)本发明提供的基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料作为活化过一硫酸氢盐的非均相催化剂可以应用于废水处理,首次将基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料应用到基于硫酸根自由基的高级氧化方法处理有机污染物的反应中去;该基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料中铁离子和钴离子均匀分散在骨架材料中可显著提高催化活性,本发明充分利用基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料中高度分散的钴和铁活性中心离子,增强过渡金属离子与过一硫酸氢盐的有效接触增强具有强氧化性的硫酸根自由基的产生,从而加快废水中的难降解有机污染物的氧化降解;高催化活性的2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料使得过一硫酸氢盐能够有效分解产生硫酸根自由基,自由基的利用率高、反应时间短、对污染物的去除效果好;(2) The iron-cobalt bimetallic-organic framework material provided by the present invention based on 2,5-dihydroxyterephthalic acid ligand can be used as a heterogeneous catalyst for activating peroxymonosulfate salt, and can be applied to wastewater treatment for the first time. The iron-cobalt bimetallic-organic framework material of 2,5-dihydroxyterephthalic acid ligand is applied to the reaction of the advanced oxidation method based on sulfate radicals for the treatment of organic pollutants; Iron ions and cobalt ions in the iron-cobalt bimetallic-organic framework material of phthalic acid ligands are uniformly dispersed in the framework material, which can significantly improve the catalytic activity. The present invention makes full use of iron based on 2,5-dihydroxyterephthalic acid ligands. The highly dispersed cobalt and iron active center ions in cobalt bimetallic-organic framework materials enhance the effective contact between transition metal ions and peroxymonosulfate salts and enhance the generation of sulfate radicals with strong oxidizing properties, thereby accelerating the difficulty of wastewater treatment. Oxidative degradation of organic pollutants; highly catalytically active 2,5-dihydroxyterephthalic acid ligand iron-cobalt bimetallic-organic framework material enables peroxymonosulfate to effectively decompose to generate sulfate radicals, free radicals High utilization rate, short reaction time and good removal of pollutants;
(3)本发明采用铁钴双金属-有机骨架材料作为非均相相催化剂对过一硫酸氢盐进行催化,在pH为3.0~11.0范围内均具有很高的催化活性,使其适用于处理的废水pH值大大拓宽,有效降低了酸碱调节费用;(3) The present invention adopts the iron-cobalt bimetallic-organic framework material as a heterogeneous catalyst to catalyze the peroxymonosulfate, which has high catalytic activity in the range of pH 3.0 to 11.0, making it suitable for treatment The pH value of the wastewater is greatly broadened, which effectively reduces the cost of acid-base adjustment;
(4)本发明采用基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料作为非均相催化剂活性高、用量少,且在常温、无需光照等条件即可高效催化过一硫酸氢盐,降低了污水处理的成本,反应后催化剂较容易从溶液中回收重复利用,无二次污染;(4) The present invention adopts the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand as a heterogeneous catalyst with high activity and low dosage, and can be used at room temperature without illumination and other conditions. High-efficiency catalysis of peroxymonosulfate reduces the cost of sewage treatment, and the catalyst after the reaction can be easily recovered and reused from the solution without secondary pollution;
(5)本发明操作简单,条件易控,催化效率高,经济可行,适合于各种有机废水的深度处理;(5) the present invention is simple to operate, easy to control the conditions, high catalytic efficiency, economical and feasible, and is suitable for advanced treatment of various organic waste water;
(6)本发明在较高pH条件下仍然保持较高的污染物去除率,此外本发明适用于各种有机废水处理,效率高、持久性好、操作方便、环境友好,能在较宽的pH范围内高效地去除废水中的有毒有害污染物,为处理有毒有害难生物降解的有机废水提供了广阔的前景。(6) The present invention still maintains a high pollutant removal rate under higher pH conditions, and in addition, the present invention is suitable for various organic wastewater treatment, with high efficiency, good durability, convenient operation, and environmental friendliness. The efficient removal of toxic and harmful pollutants in wastewater within the pH range provides a broad prospect for the treatment of toxic and harmful organic wastewater that is difficult to biodegrade.
附图说明Description of drawings
图1是本发明150°条件下制备的基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料放大倍数为1000万倍的扫描电镜图;Fig. 1 is the scanning electron microscope image that the magnification of the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand prepared under the condition of 150 ° of the present invention is 10 million times;
图2是本发明在110°条件下制备的基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料放大倍数为500万倍的扫描电镜图;Fig. 2 is the scanning electron microscope image of the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand prepared by the present invention at 110° with a magnification of 5 million times;
图3是本发明170°条件下制备的基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料放大倍数为1000万倍的扫描电镜图;Fig. 3 is the scanning electron microscope image of the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand prepared under the condition of 170° of the present invention with a magnification of 10 million times;
图4本发明150°条件下制备的基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的X射线晶体衍射图;Fig. 4 X-ray crystal diffraction pattern of the iron-cobalt bimetallic-organic framework material prepared under the condition of 150° of the present invention based on 2,5-dihydroxyterephthalic acid ligand;
图5是本发明150°条件下制备的基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的红外光谱图。Fig. 5 is the infrared spectrum of the iron-cobalt bimetallic-organic framework material prepared under the condition of 150° of the present invention based on 2,5-dihydroxyterephthalic acid ligand.
具体实施方式Detailed ways
下面结合附图和具体实施例对本发明作进一步说明,但本发明所要保护的范围并不限于此。The present invention will be further described below with reference to the accompanying drawings and specific embodiments, but the scope of protection of the present invention is not limited thereto.
本发明实施例中所使用的六水合硝酸钴(Co(NO3)2·6H2O)、四水合氯化亚铁(Cu(NO3)2)、2,5-二羟基对苯二甲酸(C8H6O6)、N,N-二甲基甲酰胺(DMF,C3H7NO)、无水乙醇(C2H6O)、过一硫酸氢钾等都是分析纯,亚甲基蓝为色谱纯,所用水都是去离子水。Cobalt nitrate hexahydrate (Co(NO 3 ) 2 ·6H 2 O), ferrous chloride tetrahydrate (Cu(NO 3 ) 2 ), 2,5-dihydroxyterephthalic acid used in the examples of the present invention (C 8 H 6 O 6 ), N,N-dimethylformamide (DMF, C 3 H 7 NO), absolute ethanol (C 2 H 6 O), potassium hydrogen peroxymonosulfate, etc. are all analytically pure, Methylene blue is chromatographically pure, and all water used is deionized water.
据统计,商业用途染料的种类已经超过100000种,世界上染料的年产量约为80万~90万吨,而我国染料年产量约为15万吨,位居世界染料产量前列。其中10%~15%的染料在生产和使用过程中会释放到环境中。而大部分染料极为稳定,进入到水体后难以自然降解,不仅造成受污染水域的色度增加,影响入射光线的量,而且进一步影响到水体中水生动植物的正常生命活动,破坏水环境的生态平衡。更为严重的是多数染料具有致癌和致畸的效应,排放到水环境中对人类和其他生物造成极大的危害。本发明考虑到染料广泛应用于医药、食品、印染和化妆品制造等行业。因此,本发明选择使用较为广泛的亚甲基蓝(MB)作为污染物的代表,研究MB的脱色降解在一定程度上可以代表难生化有机废水的降解。因此下面实施例中的有机废水选用MB溶液。According to statistics, there are more than 100,000 types of commercial dyes, and the world's annual output of dyes is about 800,000 to 900,000 tons, while my country's annual output of dyes is about 150,000 tons, ranking the forefront of the world's dye output. 10% to 15% of the dyes are released into the environment during production and use. Most of the dyes are extremely stable and difficult to degrade naturally after entering the water body, which not only increases the chromaticity of the polluted water area and affects the amount of incident light, but also further affects the normal life activities of aquatic animals and plants in the water body and destroys the ecology of the water environment. balance. What's more serious is that most dyes have carcinogenic and teratogenic effects, and their discharge into the water environment will cause great harm to humans and other organisms. The present invention takes into account that dyes are widely used in industries such as medicine, food, printing and dyeing, and cosmetic manufacturing. Therefore, in the present invention, methylene blue (MB), which is widely used, is selected as the representative of pollutants, and the decolorization and degradation of MB can represent the degradation of refractory organic wastewater to a certain extent. Therefore, the organic waste water in the following examples is selected from MB solution.
采用本发明的方法对含亚甲基蓝(MB)的有机废水进行处理。The organic waste water containing methylene blue (MB) is treated by the method of the invention.
实施例1Example 1
铁钴双金属-有机骨架材料的制备Preparation of Iron-Cobalt Bimetallic-Organic Framework Materials
(1)前驱体溶液的制备:将0.873g(3mM)Co(NO3)2·6H2O、0.596g(3mM)FeCl2·4H2O和0.498g(3mM)2,5-二羟基对苯二甲酸(DTPA)溶解于60mL N,N-二甲基甲酰胺(DMF)和乙醇混合液(DMF:乙醇=1:1)中,将上述混合液搅拌至完全溶解,得到前驱体溶液;(1) Preparation of precursor solution: 0.873 g (3 mM) Co(NO 3 ) 2 ·6H 2 O, 0.596 g (3 mM) FeCl 2 ·4H 2 O and 0.498 g (3 mM) 2,5-dihydroxyl pair Phthalic acid (DTPA) was dissolved in 60 mL of N,N-dimethylformamide (DMF) and ethanol mixture (DMF:ethanol=1:1), and the mixture was stirred until completely dissolved to obtain a precursor solution;
(2)基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料:将步骤(1)制得的前驱体溶液转移至100mL聚四氟乙烯内衬的高压反应釜中,将反应釜放入程控烘箱中,150℃溶剂热反应24h;冷却,自然降温至室温,真空泵过滤后用无水乙醇、N,N-二甲基甲酰胺(DMF)和去离子水反复洗涤得到咖啡色沉淀物;将沉淀物放入100℃的真空干燥箱中干燥12h得到黑色固体粉末,即为基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料。(2) Iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand: The precursor solution obtained in step (1) was transferred to a 100 mL polytetrafluoroethylene-lined autoclave , put the reaction kettle into a program-controlled oven, and solvothermally react at 150 °C for 24 hours; cooled, naturally cooled to room temperature, filtered with a vacuum pump, and repeated with absolute ethanol, N,N-dimethylformamide (DMF) and deionized water. Wash to obtain brown precipitate; put the precipitate into a vacuum drying oven at 100°C for 12 hours to obtain black solid powder, which is an iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand.
采用扫描电镜、X射线晶体衍射、红外对上述铁钴双金属-有机骨架材料进行表征,其中,图1是本实施例中铁钴双金属-有机骨架材料放大倍数为1000万倍扫描电镜图,图4是本实施例中铁钴双金属-有机骨架材料X射线晶体衍射图,图5是本实施例中铁钴双金属-有机骨架材料红外光谱图。从上述图示可以看出,本发明确实制备得到了铁钴双金属-有机骨架材料,其形态为规则的多面体晶体,且通过ICP-MS检测结果表明该制备方法所得材料中钴元素与铁元素摩尔比接近1:1,表明成功制备铁钴双金属-有机骨架材料。The above-mentioned iron-cobalt bimetallic-organic framework material is characterized by scanning electron microscope, X-ray crystal diffraction and infrared, wherein, Fig. 1 is a scanning electron microscope image with a magnification of 10 million times of iron-cobalt bimetallic-organic framework material in the present embodiment. Fig. 4 is the X-ray crystal diffraction diagram of the iron-cobalt bimetallic-organic framework material in this embodiment, and FIG. 5 is the infrared spectrum diagram of the iron-cobalt bimetallic-organic framework material in this embodiment. It can be seen from the above diagram that the present invention has indeed prepared an iron-cobalt bimetallic-organic framework material, which is in the form of a regular polyhedral crystal, and the detection results of ICP-MS show that the cobalt and iron elements in the material obtained by the preparation method are The molar ratio is close to 1:1, indicating the successful preparation of iron-cobalt bimetallic-organic framework materials.
实施例2Example 2
(1)前驱体溶液的制备:将0.873g(3mM)Co(NO3)2·6H2O、0.596g(3mM)FeCl2·4H2O和0.498g(3mM)2,5-二羟基对苯二甲酸(DTPA)溶解于60mL N,N-二甲基甲酰胺(DMF)和乙醇混合液(DMF:乙醇=1:1)中,将上述混合液搅拌至完全溶解,得到前驱体溶液;(1) Preparation of precursor solution: 0.873 g (3 mM) Co(NO 3 ) 2 ·6H 2 O, 0.596 g (3 mM) FeCl 2 ·4H 2 O and 0.498 g (3 mM) 2,5-dihydroxyl pair Phthalic acid (DTPA) was dissolved in 60 mL of N,N-dimethylformamide (DMF) and ethanol mixture (DMF:ethanol=1:1), and the mixture was stirred until completely dissolved to obtain a precursor solution;
(2)基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料:将步骤(1)制得的前驱体溶液转移至100mL聚四氟乙烯内衬的高压反应釜中,将反应釜放入程控烘箱中,110℃溶剂热反应24h;冷却,自然降温至室温,真空泵过滤后用无水乙醇、N,N-二甲基甲酰胺(DMF)和去离子水反复洗涤得到咖啡色沉淀物;将沉淀物放入100℃的真空干燥箱中干燥12h得到黑色固体粉末,即为基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料。(2) Iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand: The precursor solution obtained in step (1) was transferred to a 100 mL polytetrafluoroethylene-lined autoclave , put the reaction kettle into a program-controlled oven, and solvothermally react at 110 °C for 24 hours; cooled, naturally cooled to room temperature, filtered by a vacuum pump, and repeated with absolute ethanol, N,N-dimethylformamide (DMF) and deionized water. Wash to obtain brown precipitate; put the precipitate into a vacuum drying oven at 100°C for 12 hours to obtain black solid powder, which is an iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand.
采用扫描电镜对上述铁钴双金属-有机骨架材料进行表征,其中,图2是本实施例中铁钴双金属-有机骨架材料放大倍数为500万倍扫描电镜图。The above iron-cobalt bimetallic-organic framework material is characterized by scanning electron microscope, wherein, FIG. 2 is a scanning electron microscope image of the iron-cobalt bimetallic-organic framework material in this embodiment with a magnification of 5 million times.
实施例3Example 3
(1)前驱体溶液的制备:将0.873g(3mM)Co(NO3)2·6H2O、0.596g(3mM)FeCl2·4H2O和0.498g(3mM)2,5-二羟基对苯二甲酸(DTPA)溶解于60mL N,N-二甲基甲酰胺(DMF)和乙醇混合液(DMF:乙醇=1:1)中,将上述混合液搅拌至完全溶解,得到前驱体溶液;(1) Preparation of precursor solution: 0.873 g (3 mM) Co(NO 3 ) 2 ·6H 2 O, 0.596 g (3 mM) FeCl 2 ·4H 2 O and 0.498 g (3 mM) 2,5-dihydroxyl pair Phthalic acid (DTPA) was dissolved in 60 mL of N,N-dimethylformamide (DMF) and ethanol mixture (DMF:ethanol=1:1), and the mixture was stirred until completely dissolved to obtain a precursor solution;
(2)基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料:将步骤(1)制得的前驱体溶液转移至100mL聚四氟乙烯内衬的高压反应釜中,将反应釜放入程控烘箱中,170℃溶剂热反应24h;冷却,自然降温至室温,真空泵过滤后用无水乙醇、N,N-二甲基甲酰胺(DMF)和去离子水反复洗涤得到咖啡色沉淀物;将沉淀物放入100℃的真空干燥箱中干燥12h得到黑色固体粉末,即为基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料。(2) Iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand: The precursor solution obtained in step (1) was transferred to a 100 mL polytetrafluoroethylene-lined autoclave , put the reaction kettle into a program-controlled oven, solvothermally react at 170 °C for 24 hours; cool, naturally cool to room temperature, filter with a vacuum pump and repeat with absolute ethanol, N,N-dimethylformamide (DMF) and deionized water. Wash to obtain brown precipitate; put the precipitate into a vacuum drying oven at 100°C for 12 hours to obtain black solid powder, which is an iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand.
采用扫描电镜对上述铁钴双金属-有机骨架材料进行表征,其中,图3是本实施例中铁钴双金属-有机骨架材料放大倍数为1000万倍扫描电镜图。The above iron-cobalt bimetallic-organic framework material is characterized by scanning electron microscope, wherein, FIG. 3 is a scanning electron microscope image of the iron-cobalt bimetallic-organic framework material in this embodiment with a magnification of 10 million times.
实施例4Example 4
加入基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料和过一硫酸氢钾、基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料或过一硫酸氢钾的条件下MB的去除率Addition of iron-cobalt bimetallic-organic framework materials based on 2,5-dihydroxyterephthalic acid ligands and potassium hydrogen peroxymonosulfate, iron-cobalt bimetallic-organic frameworks based on 2,5-dihydroxyterephthalic acid ligands Removal rate of MB under the condition of framework material or potassium hydrogen persulfate
采用锥形瓶作为反应器,废水反应体积为100mL,废水含亚甲基蓝的初始浓度为0.2mM,pH为6.1;设置三个处理组:其中,处理组1同时往反应瓶中加入基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料(实施例1方法制备所得)和过一硫酸氢钾(终浓度分别为0.05g/L和2mM),处理组2单独加入基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料(终浓度为0.1g/L),不需加入过一硫酸氢钾;处理组3单独加入过一硫酸氢钾(终浓度为2mM),不需加入基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料;将上述三个处理组反应瓶置于震荡床中,在转速为100rpm,温度为25℃的条件下进行反应并定时检测反应体系中的MB含量,计算MB去除率;不同处理组MB去除率的比较结果见表1。The conical flask was used as the reactor, the reaction volume of the wastewater was 100 mL, the initial concentration of methylene blue in the wastewater was 0.2 mM, and the pH was 6.1; three treatment groups were set up: among them, treatment group 1 was added to the reaction flask at the same time based on 2,5- The iron-cobalt bimetallic-organic framework material of dihydroxyterephthalic acid ligand (prepared by the method of Example 1) and potassium hydrogen peroxymonosulfate (final concentrations were 0.05 g/L and 2 mM, respectively), treatment group 2 was added separately based on 2,5-Dihydroxyterephthalic acid ligand iron-cobalt bimetallic-organic framework material (final concentration 0.1g/L), no need to add potassium hydrogen peroxymonosulfate; treatment group 3 added potassium hydrogen peroxymonosulfate alone (final concentration is 2mM), no need to add iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand; the reaction flasks of the above three treatment groups were placed in a shaking bed, and the rotation speed was The reaction was carried out at 100 rpm and a temperature of 25 °C, and the MB content in the reaction system was detected regularly to calculate the MB removal rate; the comparison results of the MB removal rate of different treatment groups are shown in Table 1.
表1Table 1
表1结果表明,单独基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料和单独过一硫酸氢钾体系都未能对MB进行有效降解去除,而基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料活化过一硫酸氢钾体系中对MB的处理效果非常显著,反应30min后,MB的去除率达到98.2%,说明本发明能够快速有效地处理难生化废水。The results in Table 1 show that both the iron-cobalt bimetallic-organic framework materials based on 2,5-dihydroxyterephthalic acid ligand alone and the potassium hydrogen peroxymonosulfate system alone failed to effectively degrade and remove MB, while those based on 2, 5-dihydroxyterephthalic acid ligand iron-cobalt bimetallic-organic framework material activated potassium hydrogen persulfate system in the treatment effect of MB is very significant, after 30min of reaction, the removal rate of MB reached 98.2%, indicating the present invention It can quickly and effectively treat difficult-to-biochemical wastewater.
实施例5Example 5
基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料活化过一硫酸氢钾在酸性、中性及碱性条件下MB的去除率Removal of MB under acidic, neutral and alkaline conditions by using iron-cobalt bimetallic-organic frameworks based on 2,5-dihydroxyterephthalic acid ligands to activate potassium peroxymonosulfate
采用锥形瓶作为反应器,废水反应体积为100mL,废水含MB的初始浓度为0.2mM;设置四个处理组:其中,反应开始前往反应瓶中加入过一硫酸氢钾使其浓度为2mM,并将废水的pH值分别调为3.0(处理组1)、5.0(处理组2)、7.0(处理组3)、9.0(处理组4)和11.0(处理组5),然后向反应瓶中投加基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料(实施例1方法制备所得)使其反应浓度为0.05g/L,并将反应瓶置于震荡床中,在转速为100rpm,温度为25℃的条件下进行反应并定时检测反应体系中的MB含量,计算MB去除率;pH值对基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料活化过一硫酸氢钾降解MB的影响结果见表2。The conical flask was used as the reactor, the reaction volume of the wastewater was 100 mL, and the initial concentration of MB in the wastewater was 0.2 mM; four treatment groups were set: among them, the reaction began to go to the reaction flask and potassium hydrogen persulfate was added to make the concentration 2 mM, The pH value of the wastewater was adjusted to 3.0 (treatment group 1), 5.0 (treatment group 2), 7.0 (treatment group 3), 9.0 (treatment group 4) and 11.0 (treatment group 5), and then poured into the reaction flask. Add the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand (prepared by the method of Example 1) to make the reaction concentration 0.05g/L, and place the reaction flask in the shaking bed , under the condition of rotating speed of 100rpm and temperature of 25℃, the MB content in the reaction system was detected regularly, and the MB removal rate was calculated; Table 2 shows the effect of metal-organic framework activated potassium peroxymonosulfate on MB degradation.
表2Table 2
表2结果表明,铁钴双金属-有机骨架材料活化过一硫酸氢钾氧化方法在酸性、近中性条件下均能对MB具有非常好的降解效果,节省了投酸费用,保证了该高级氧化技术的高效性。pH=5.0条件下处理效果最佳,基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的用量少,活化效率高。The results in Table 2 show that the iron-cobalt bimetallic-organic framework material activated potassium hydrogen persulfate oxidation method can have a very good degradation effect on MB under acidic and near-neutral conditions, saving the cost of acid feeding and ensuring the high-grade Efficiency of oxidation technology. The treatment effect is the best under the condition of pH=5.0, and the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand has less dosage and high activation efficiency.
实施例6Example 6
基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料不同投加量对MB去除率的影响Effects of different dosages of Fe-Co bimetallic-organic framework based on 2,5-dihydroxyterephthalic acid ligand on MB removal rate
采用锥形瓶作为反应器,废水反应体积为100mL,废水含MB的初始浓度为0.2mM,pH为6.1,反应开始前往反应瓶中加入过一硫酸氢钾使其浓度为2mM,设置四个处理组:其中,向反应瓶中投加基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料(实例3方法制备所得)使其反应浓度为0.05g/L(处理组1)、0.1g/L(处理组2)、0.2g/L(处理组3)和0.3g/L(处理组4),最后将反应瓶置于震荡床中,在转速为100rpm,温度为25℃的条件下进行反应并定时检测反应体系中的MB含量,计算MB去除率;基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料的浓度对活化过一硫酸氢钾降解MB的影响结果见表3。The conical flask was used as the reactor, the reaction volume of the wastewater was 100 mL, the initial concentration of MB in the wastewater was 0.2 mM, and the pH was 6.1. The reaction began to go to the reaction flask and potassium hydrogen persulfate was added to make the concentration 2 mM, and four treatments were set. Group: wherein, the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand (prepared by the method of Example 3) was added to the reaction flask to make the reaction concentration 0.05g/L (treatment Group 1), 0.1g/L (treatment group 2), 0.2g/L (treatment group 3) and 0.3g/L (treatment group 4), and finally the reaction flask was placed in a shaking bed, and the rotating speed was 100 rpm and the temperature was 100 rpm. The reaction was carried out under the condition of 25 °C and the MB content in the reaction system was detected regularly to calculate the MB removal rate; Table 3 shows the effect of potassium bisulfate on the degradation of MB.
表3table 3
表3结果表明,基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料浓度对活化过一硫酸氢钾降解MB有一定的影响,随着其浓度的增加,MB的降解率增加,基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料浓度为0.1g/L时对MB的降解速率最高,在10min内100%降解MB。说明基于2,5-二羟基对苯二甲酸配体的铁钴双金属-有机骨架材料活性高,用量少。因此在难生化处理的有机废水中具有广阔的应用前景。The results in Table 3 show that the concentration of iron-cobalt bimetallic-organic framework materials based on 2,5-dihydroxyterephthalic acid ligands has a certain effect on the degradation of MB by activated potassium peroxymonosulfate. With the increase of its concentration, MB The degradation rate of 2,5-dihydroxyterephthalic acid ligand-based iron-cobalt bimetallic-organic framework material was the highest when the concentration of 0.1 g/L was 0.1 g/L, and 100% of MB was degraded within 10 min. It shows that the iron-cobalt bimetallic-organic framework material based on 2,5-dihydroxyterephthalic acid ligand has high activity and low dosage. Therefore, it has broad application prospects in organic wastewater that is difficult to biochemically treat.
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,其他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 embodiments are preferred embodiments of the present invention, but the embodiments of the present invention are not limited by the above-mentioned embodiments, and any other changes, modifications, substitutions, combinations, The simplification should be equivalent replacement manners, which are all included in the protection scope of the present invention.
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