CN109107608A - A kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst and preparation method thereof - Google Patents

A kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst and preparation method thereof Download PDF

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CN109107608A
CN109107608A CN201710536281.6A CN201710536281A CN109107608A CN 109107608 A CN109107608 A CN 109107608A CN 201710536281 A CN201710536281 A CN 201710536281A CN 109107608 A CN109107608 A CN 109107608A
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photochemical catalyst
uranyl
paranitrobenzoic acid
complexes
acid complexes
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任亚男
许伟
郑岳青
朱红林
周林霞
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Ningbo University
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    • B01J35/39
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/16Catalysts comprising hydrides, coordination complexes or organic compounds containing coordination complexes
    • B01J31/22Organic complexes
    • B01J31/2204Organic complexes the ligands containing oxygen or sulfur as complexing atoms
    • B01J31/2208Oxygen, e.g. acetylacetonates
    • B01J31/2213At least two complexing oxygen atoms present in an at least bidentate or bridging ligand
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C201/00Preparation of esters of nitric or nitrous acid or of compounds containing nitro or nitroso groups bound to a carbon skeleton
    • C07C201/06Preparation of nitro compounds
    • C07C201/12Preparation of nitro compounds by reactions not involving the formation of nitro groups
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C205/00Compounds containing nitro groups bound to a carbon skeleton
    • C07C205/49Compounds containing nitro groups bound to a carbon skeleton the carbon skeleton being further substituted by carboxyl groups
    • C07C205/57Compounds containing nitro groups bound to a carbon skeleton the carbon skeleton being further substituted by carboxyl groups having nitro groups and carboxyl groups bound to carbon atoms of six-membered aromatic rings of the carbon skeleton
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07FACYCLIC, CARBOCYCLIC OR HETEROCYCLIC COMPOUNDS CONTAINING ELEMENTS OTHER THAN CARBON, HYDROGEN, HALOGEN, OXYGEN, NITROGEN, SULFUR, SELENIUM OR TELLURIUM
    • C07F5/00Compounds containing elements of Groups 3 or 13 of the Periodic System
    • C07F5/003Compounds containing elements of Groups 3 or 13 of the Periodic System without C-Metal linkages
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2531/00Additional information regarding catalytic systems classified in B01J31/00
    • B01J2531/02Compositional aspects of complexes used, e.g. polynuclearity
    • B01J2531/0238Complexes comprising multidentate ligands, i.e. more than 2 ionic or coordinative bonds from the central metal to the ligand, the latter having at least two donor atoms, e.g. N, O, S, P
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2531/00Additional information regarding catalytic systems classified in B01J31/00
    • B01J2531/30Complexes comprising metals of Group III (IIIA or IIIB) as the central metal
    • B01J2531/39Actinides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07BGENERAL METHODS OF ORGANIC CHEMISTRY; APPARATUS THEREFOR
    • C07B2200/00Indexing scheme relating to specific properties of organic compounds
    • C07B2200/13Crystalline forms, e.g. polymorphs

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  • Health & Medical Sciences (AREA)
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  • Inorganic Chemistry (AREA)
  • Toxicology (AREA)
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  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

The invention discloses a kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst, the molecular formula of the photochemical catalyst is (H2‑bipy)[(UO2)43‑O)2(p‑nba)6], bipy is 4 in molecular formula, 4 '-bipyridyls, Hp-nba is paranitrobenzoic acid, the catalyst is under the irradiation of xenon source, in 300 minutes by concentration be 40mg/L quadracycline solution degradation to 9.1%, be a kind of Complexes of Uranyl photochemical catalyst for having catalytic degradation performance to quadracycline under visible light.

Description

A kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst and preparation method thereof
Technical field
The present invention relates to photochemical catalysts, and in particular to a kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst and its preparation Method.
Background technique
Penicillin is had found from nineteen twenty-eight Alexander Fleming, and William Bei Nade in 1948 is from actinomycetes Aureomycin is extracted in streptomycete, up to the present, the type of antibiotic has reached thousands of kinds, is widely used in treating human body disease Disease, prevention livestock and poultry, aquatic products bacterial disease in.However, life and medically antibiotic excessively use and abuse, pharmacy The discharge of the waste water such as enterprise, animal feed and culture fishery, so that contain a large amount of antibiotic pollutant in water environment at present, The environmental problem got worse is caused, if not effectively removed, Drinking w ater, ecological environment and human health are generated Long-term potential threat.The common technique of antibiotic has physical method, chemical method, bioanalysis, photocatalytic method in processing waste water at present Deng.Wherein, physical method carries out the processing of antibiotic waste water in a manner of adsorbing pollutant, and there are poor selectivities and cannot be continuous The disadvantages of operation;Biological rule has the function that removal antibiotic using the oxydasis and reduction organic molecule of microorganism, The problems such as it is not thorough there are operating condition harshness, microorganism poisoning and degradation;The chemistry that chemical rule passes through between substance is anti- The antibiotic in waste water should be removed, but will cause secondary pollution after treatment, and higher cost, in the industrial production by one Fixed limitation;And photocatalysis technology is a kind of green technology for having important application prospect in the energy and environmental area, advantage It is: applied widely, reaction rate is fast;Theoretically with permineralization pollutant and it can will not generate secondary pollution;Operating cost It is low.Therefore, photocatalysis technology has broad application prospects in terms of removing organic pollutant.Meanwhile the preparation of photochemical catalyst Also result in the extensive concern of people.
Organic Pollutants in Wastewater can be oxidized to H at room temperature by semiconductor light-catalyst2O、CO2Or inorganic ions etc., and It is without secondary pollution.Currently, catalyst most commonly used in photocatalysis technology is TiO2Semiconductor material, the material is with it to biology It is nontoxic, chemical property is stable, high catalytic efficiency under fast light burn into ultraviolet light, it is cheap and easy to get the advantages that, be acknowledged as at present most Good photochemical catalyst.Such as the application for a patent for invention of Publication No. CN102698727A, discloses and a kind of prepare high thermal stability Supported titanium2The method of photochemical catalyst;But TiO2There are still fatal disadvantages in practical applications for catalysis material: light Response range is narrow, because the ultraviolet light of solar energy 4% can only be utilized, and quantum efficiency is low.In order to promote it visible The photocatalysis performance in light region, people are to TiO2A large amount of study on the modification is expanded, such as dye photoactivation, semiconductors coupling, gold Belong to doping, nonmetal doping etc., as the patent of invention of Publication No. CN103007938A discloses a kind of Cu doping vario-property TiO2Photochemical catalyst and preparation method thereof, but these means still have many deficiencies.Therefore, exploitation novel photocatalysis material is Solve the key of tetracycline antibiotics pollution problem in waste water.Uranyl ion have unique visible light wave range it is strong absorption with Response has higher photocatalysis efficiency, is expected to solve TiO2Optical response range present in photochemical catalyst is narrow, quantum efficiency is low The disadvantages of, become the photochemical catalyst for having much application potential, as the patent of invention of Publication No. CN103447090A discloses one kind P-methyl benzoic acid uranyl complex photocatalyst, the catalyst have excellent degradation property under xenon lamp to rhodamine B.And And degradation of the uranyl base complex for antibiotic pollutant in waste water, the improvement for antibiotic pollutant in environment provide One practicable approach, also excellent basis has been established in the exploitation for uranyl based photocatalyst, and therefore, the present invention uses water Thermal method has synthesized a kind of Complexes of Uranyl photochemical catalyst for having catalytic degradation performance to quadracycline under visible light.
Summary of the invention
Technical problem to be solved by the invention is to provide a kind of paranitrobenzoic acid uranyl of degradable quadracycline Complex photochemical catalyst.
The technical scheme of the invention to solve the technical problem is: a kind of paranitrobenzoic acid Complexes of Uranyl light Catalyst, molecular formula are (H2-bipy)[(UO2)43-O)2(p-nba)6], bipy=4 in molecular formula, 4 '-bipyridyls, Hp- Nba=paranitrobenzoic acid.The cell parameter of the paranitrobenzoic acid Complexes of Uranyl photocatalyst crystals are as follows:α=85.07 (3) °, β=74.65 (3) °, γ (°)=73.38 (3) ° it is, anorthic system, belongs to P-1 space group.
Compared with the prior art, the advantages of the present invention are as follows a kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalysts, should The molecular formula of photochemical catalyst is (H2-bipy)[(UO2)43-O)2(p-nba)6], bipy is 4,4'-Bipyridine in molecular formula, Hp-nba is paranitrobenzoic acid, the degradable quadracycline of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst, and this is right Methyl benzoic acid Complexes of Uranyl photochemical catalyst can use centrifugal separation method recycling and reusing, and the catalyst is avoided to may cause Secondary pollution.
Detailed description of the invention
Fig. 1 is the molecular structure of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst of the present invention;
Fig. 2 is that the PXRD map of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst of the present invention and monocrystalline simulate PXRD map Comparison diagram;
Fig. 3 is photocatalytic degradation curve of the paranitrobenzoic acid Complexes of Uranyl photochemical catalyst of the present invention to quadracycline Figure.
Specific embodiment
The present invention will be described in further detail below with reference to the embodiments of the drawings.
Embodiment 1
It weighs 0.25mmol uranium acetate and is dissolved in 5mL H2In O, yellow solution is dissolved to obtain, separately weighs 0.5mmol to nitre The 4,4'-Bipyridine of yl benzoic acid and 0.2mmol are added in above-mentioned mixed solution and stir, and solution becomes cloudy, and continues to stir 30min measures pH=2.11, and mixed solution is transferred in the ptfe autoclave liner of 23mL, sealing, and 140 72h is kept at DEG C.Yellow product is obtained after cooling, which is molecular formula (H2-bipy)[(UO2)43-O)2(Hp- nba)6] a kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst.By yellow product grind into powder, weighs 48mg and be placed in 60mL contains in the aqueous solution that concentration is 40mg/L quadracycline, is placed in photochemical catalyst reactor, turn on agitator, Under xenon lamp 300W radiation of visible light, the xenon lamp for being 300W with light source, it is seen that photocatalytic degradation is carried out to it under light, every 30min Suitable solution is taken, it, 300 minutes can with the variation of quadracycline in ultraviolet-visible spectrophotometer monitoring solution after centrifugation By the quadracycline degradation 91.9% in aqueous solution, photocatalytic degradation curve graph as shown in Figure 3 is obtained, control experiment is not It is carried out under conditions of addition paranitrobenzoic acid Complexes of Uranyl photochemical catalyst, step is same as above.
As seen from Figure 3, it in the case where 300W xenon lamp irradiates no catalyst, does not add and states hydrochloric tetracycline simultaneously There is no degradations, and after above-mentioned catalyst is added, obvious degradation occurs for quadracycline, after 300min, degradation rate 91.9%, It is the photochemical catalyst for having degradation to quadracycline.The complex can use the method recycling of centrifuge separation as photochemical catalyst It recycles.Use 2 θ angular range of Bruker D8 Focus powder diffractometer for 5-50 °, with the scanning speed of 10 °/min to this Complexes of Uranyl photochemical catalyst is scanned, and collects the powder diffraction spectrum (PXRD) of sample at room temperature, and simulate with monocrystalline PXRD figure comparison, perfect can be fitted, and illustrate that product is pure phase, purity is not less than 99%.
Embodiment 2
Substantially the same manner as Example 1, different only uranium acetates are substituted by uranyl nitrate.

Claims (3)

1. a kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst, it is characterised in that the molecule of the Complexes of Uranyl photochemical catalyst Formula is (H2-bipy)[(UO2)43-O)2(p-nba)6], wherein bipy=4,4 '-bipyridyls, Hp-nba=p-nitrophenyl first Acid, it is characterised in that the cell parameter of the crystal of the paranitrobenzoic acid Complexes of Uranyl photochemical catalyst are as follows:α (°)=85.07 (3) °, β (°)=74.65 (3) °, γ (°)=73.38 (3) °, the photochemical catalyst are that can lead to the yellow powder sieved with 100 mesh sieve, and purity is not less than 99%, under visible light There is the Complexes of Uranyl photochemical catalyst of catalytic degradation performance to quadracycline.
2. the preparation method of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst described in claim 1, it is characterised in that step It is as follows:
A) it weighs 0.1~0.5mmol uranium acetate and is dissolved in 3~10mL H2In O, dissolve yellow solution is stand-by;
B) above-mentioned steps a) mixing is added in the 4,4'-Bipyridine for weighing 0.2~1mmol paranitrobenzoic acid and 0.1~0.5mmol It is stirred in solution, solution becomes cloudy, and continues 10~60min of stirring;
C) mixed liquor of step b) is transferred in the ptfe autoclave liner of 23mL, seals 120~160 DEG C of reactions 48 ~72h, is cooled to room temperature, and yellow chunked pieces body is ground into the powder sieved with 100 mesh sieve by filtering, obtains purity not less than 99% Paranitrobenzoic acid uranyl photochemical catalyst.
3. the preparation method of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst as claimed in claim 2, it is characterised in that nitre Sour uranyl substitutes uranium acetate.
CN201710536281.6A 2017-06-23 2017-06-23 A kind of paranitrobenzoic acid Complexes of Uranyl photochemical catalyst and preparation method thereof Pending CN109107608A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109939739A (en) * 2019-04-03 2019-06-28 东华理工大学 A kind of 5- nitro-l,2,3 benzene tricarboxylic acid Complexes of Uranyl photochemical catalyst and preparation method thereof
CN110003248A (en) * 2019-04-03 2019-07-12 东华理工大学 A kind of polycarboxylic acid Complexes of Uranyl photochemical catalyst and preparation method thereof
CN111495430A (en) * 2020-04-21 2020-08-07 周口师范学院 Target-uranyl-based poly tungstate photocatalyst and preparation method and application thereof
CN114558621A (en) * 2022-03-08 2022-05-31 西安医学院 Bis (2-carboxyethyl) isocyanurate uranyl complex photocatalyst and method

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EP0034677A1 (en) * 1980-02-25 1981-09-02 Exxon Research And Engineering Company Novel uranyl compounds employing a strong base
CN103447090A (en) * 2013-07-23 2013-12-18 宁波大学 P-methyl benzoic acid uranyl complex photocatalyst
CN104607242A (en) * 2013-11-01 2015-05-13 宁波大学 5-hydroxyl m-phthalic acid uranyl complex photocatalyst

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EP0034677A1 (en) * 1980-02-25 1981-09-02 Exxon Research And Engineering Company Novel uranyl compounds employing a strong base
CN103447090A (en) * 2013-07-23 2013-12-18 宁波大学 P-methyl benzoic acid uranyl complex photocatalyst
CN104607242A (en) * 2013-11-01 2015-05-13 宁波大学 5-hydroxyl m-phthalic acid uranyl complex photocatalyst

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HAO-HONG LI ET AL.: "Incorporating Guest Molecules into Honeycomb Structures Constructed from Uranium(VI)-Polycarboxylates: Structural Diversities and Photocatalytic Activities for the Degradation of Organic Dye", 《CRYST. GROWTH DES.》 *
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109939739A (en) * 2019-04-03 2019-06-28 东华理工大学 A kind of 5- nitro-l,2,3 benzene tricarboxylic acid Complexes of Uranyl photochemical catalyst and preparation method thereof
CN110003248A (en) * 2019-04-03 2019-07-12 东华理工大学 A kind of polycarboxylic acid Complexes of Uranyl photochemical catalyst and preparation method thereof
CN110003248B (en) * 2019-04-03 2022-09-02 东华理工大学 Polycarboxylic acid uranyl complex photocatalyst and preparation method thereof
CN111495430A (en) * 2020-04-21 2020-08-07 周口师范学院 Target-uranyl-based poly tungstate photocatalyst and preparation method and application thereof
CN111495430B (en) * 2020-04-21 2023-03-14 周口师范学院 Target-uranyl-based poly tungstate photocatalyst and preparation method and application thereof
CN114558621A (en) * 2022-03-08 2022-05-31 西安医学院 Bis (2-carboxyethyl) isocyanurate uranyl complex photocatalyst and method

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