CN114682100A - Preparation method of magnetic graphene-based MOFs hybrid membrane - Google Patents

Preparation method of magnetic graphene-based MOFs hybrid membrane Download PDF

Info

Publication number
CN114682100A
CN114682100A CN202210323163.8A CN202210323163A CN114682100A CN 114682100 A CN114682100 A CN 114682100A CN 202210323163 A CN202210323163 A CN 202210323163A CN 114682100 A CN114682100 A CN 114682100A
Authority
CN
China
Prior art keywords
magnetic graphene
magnetic
graphene
based mofs
preparation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202210323163.8A
Other languages
Chinese (zh)
Inventor
李颖
丁竹
高仲
黄艳凤
王学彬
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Gaoshi Ruilian Tianjin Photoelectric Technology Co ltd
Tianjin Polytechnic University
Original Assignee
Gaoshi Ruilian Tianjin Photoelectric Technology Co ltd
Tianjin Polytechnic University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Gaoshi Ruilian Tianjin Photoelectric Technology Co ltd, Tianjin Polytechnic University filed Critical Gaoshi Ruilian Tianjin Photoelectric Technology Co ltd
Priority to CN202210323163.8A priority Critical patent/CN114682100A/en
Publication of CN114682100A publication Critical patent/CN114682100A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D67/00Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
    • B01D67/0079Manufacture of membranes comprising organic and inorganic components
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/02Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor characterised by their properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/14Dynamic membranes
    • B01D69/141Heterogeneous membranes, e.g. containing dispersed material; Mixed matrix membranes
    • B01D69/148Organic/inorganic mixed matrix membranes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/02Inorganic material
    • B01D71/021Carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/06Organic material
    • B01D71/76Macromolecular material not specifically provided for in a single one of groups B01D71/08 - B01D71/74
    • B01D71/82Macromolecular material not specifically provided for in a single one of groups B01D71/08 - B01D71/74 characterised by the presence of specified groups, e.g. introduced by chemical after-treatment
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/30Chemical resistance
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/46Magnetic properties
    • 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
    • C02F2101/305Endocrine disruptive agents
    • 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
    • C02F2101/345Phenols

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Dispersion Chemistry (AREA)
  • Manufacturing & Machinery (AREA)
  • Carbon And Carbon Compounds (AREA)

Abstract

A preparation method of a magnetic graphene-based MOFs hybrid film comprises the steps of firstly preparing a magnetic graphene material by a hydrothermal reduction method, then loading ZnO on the surface of the magnetic graphene material, and synthesizing the magnetic graphene-based MOFs hybrid film by in-situ growth by taking the ZnO as a metal source. The prepared magnetic graphene-based MOFs hybrid membrane can be used for efficiently adsorbing and removing phenol endocrine disruptors in tap water. The invention has the advantages that: the preparation method of the magnetic graphene-based MOFs hybrid membrane is reasonable in process and easy to implement; when the material is used for removing endocrine disruptors, the material has good chemical stability and reusability, and is easy to actively adsorb, identify and separate the phenolic endocrine disruptors; the preparation method has strong magnetic responsiveness, presettability and practicability, greatly improves the use efficiency of the MOFs hybrid membrane, and widens the application range of the MOFs material.

Description

Preparation method of magnetic graphene-based MOFs hybrid membrane
Technical Field
The invention relates to preparation of MOFs hybrid membranes, in particular to a preparation method of a magnetic graphene-based MOFs hybrid membrane.
Background
With the wide application of Phenolic fine chemical raw materials, pesticides, preservatives, antioxidants and the like in industrial and agricultural production, the pollution problem of Phenolic Endocrine Disrupting Chemicals (pEDCs) in water environment is becoming more and more serious. The pEDCs mainly comprise Alkylphenol (APs), bisphenol A (BPA) and Chlorophenol (CPs), and have attracted extensive attention for their environmental persistence, bioaccumulation, high toxicity and estrogen-like activity. BPA is ubiquitous in human daily life, mineral water bottles, medical instruments and food packages have 'miniature', and long-term use of BPA causes non-negligible BPA pollution in the environment. Especially, the problem of BPA pollution in water environment is closely related to the safety of drinking water, and ultra-trace BPA in water quality can possibly interfere the endocrine function of human or animals to cause various diseases such as cancer, hematopathy, diabetes, birth defects and the like, thereby having certain potential threat to the ecological environment and human health.
Graphene materials have generally attracted attention in the fields of environmental, chemical and biomedical applications due to their properties of dispersibility, hydrophilicity, polymer compatibility, and the like. The preparation of the functionalized graphene composite material can be designed into various ways according to the target functionality, and at present, the preparation mainly focuses on two aspects of preparation by taking functional nanoparticles as precursors and direct coordination assembly preparation of the functional nanoparticles and graphene. The functionalized graphene composite material is an important research direction in the application field of graphene, shows excellent performance in the fields of energy storage, liquid crystal devices, electronic devices, biological materials, sensing materials, catalyst carriers and the like, and has a wide application prospect.
The MOFs material has the advantages of large specific surface area, high catalytic activity, capability of performing chemical modification according to needs and the like, and has become a research hotspot in many fields. The characteristics of the MOFs material such as high specific surface area, high catalytic activity and the like can obviously improve the enrichment efficiency of the sensitive material on target molecules and sense detection signals. The design and synthesis of the magnetic graphene-based MOFs hybrid membrane is a composite membrane material obtained by selecting magnetic graphene as a substrate and growing the MOFs membrane on the surface in situ. The magnetic graphene-based MOFs hybrid membrane has the advantages that the structure is a two-dimensional thin-film structure, the MOFs film grown in situ in the structure is thin and compact, most catalytic active sites are exposed on the surface of the composite membrane, the stability between the catalytic active sites and the magnetic graphene is good, and the preparation and application research of the magnetic graphene-based MOFs hybrid membrane is a brand new direction in the research field of MOFs materials.
Disclosure of Invention
The invention aims to overcome the defects of uneven MOFs doping amount, weaker combination stability with a supporting matrix and the like in the structure of a conventional massive and granular MOFs composite material, provides a preparation method of a magnetic graphene-based MOFs hybrid membrane, and applies the magnetic graphene-based MOFs hybrid membrane to the adsorption and removal of trace phenol secretion interferents in a water environment.
The technical scheme of the invention is as follows:
a preparation method of a magnetic graphene-based MOFs hybrid film comprises the steps of firstly preparing a magnetic graphene material by a hydrothermal reduction method, then loading ZnO on the surface of the magnetic graphene material, and synthesizing the magnetic graphene-based MOFs hybrid film by in-situ growth by taking the ZnO as a metal source.
Further, the magnetic graphene material is obtained by the following method that ferric chloride hexahydrate is dissolved in a mixed solution of ethylene glycol and diethylene glycol, graphene oxide is added after ultrasonic treatment and is uniformly mixed, sodium citrate and anhydrous sodium acetate are added for ultrasonic dissolution, and the mixed solution is subjected to high-temperature reaction, washing and drying.
Further, the ZnO modified magnetic graphene is obtained by respectively dissolving a magnetic graphene material and zinc oxide in absolute ethyl alcohol, dropping the zinc oxide into absolute ethyl alcohol dispersion liquid of the magnetic graphene material after ultrasonic treatment, and performing ultrasonic treatment, washing, magnetic separation on a product and drying.
Further, the magnetic graphene-based MOFs hybrid membrane is obtained by dissolving ZnO modified magnetic graphene and dimethyl imidazole in DMF and H2And in the mixed solution of O, reacting the mixed solution after ultrasonic treatment to obtain a product, washing and drying to obtain the magnetic graphene-based MOFs hybrid membrane.
A preparation method of a magnetic graphene-based MOFs hybrid membrane comprises the following steps:
1) preparation of magnetic graphene material
Dissolving 1.62g of ferric chloride hexahydrate in 40mL of a mixed solution of ethylene glycol and diethylene glycol, performing ultrasonic treatment for 10min, adding 50-200 mg of graphene oxide into the uniformly mixed solution, uniformly mixing the graphene oxide and the uniformly mixed solution, adding 0.3529g of sodium citrate and 4.32g of anhydrous sodium acetate, performing ultrasonic dissolution, simultaneously performing magnetic stirring for 30min, putting the mixed solution into a reaction kettle, reacting for 12h at 200 ℃, naturally cooling, taking out, washing a product obtained by the reaction with anhydrous ethanol for 5 times, and performing vacuum drying at 60 ℃ to obtain magnetic graphene;
2) preparation of ZnO modified magnetic graphene
Respectively dissolving 50-100 mg of magnetic graphene material and 20-50 mg of zinc oxide in absolute ethyl alcohol, carrying out ultrasonic treatment for 120min, slowly dropping the zinc oxide subjected to ultrasonic treatment into the absolute ethyl alcohol dispersion liquid of the magnetic graphene material, carrying out ultrasonic treatment for 60min, washing the product for 5 times with absolute ethyl alcohol, carrying out magnetic separation on the product, and carrying out vacuum drying at 60 ℃ to obtain ZnO modified magnetic graphene;
3) preparation of magnetic graphene-based MOFs hybrid membrane
10-30 mg of ZnO modified magnetic graphene and 50-100 mg of diMethylimidazole dissolved in 13.5mL DMF and 2.5mL H2And (3) carrying out ultrasonic treatment in the mixed solution in the O for 60min, putting the mixed solution after ultrasonic treatment into a polytetrafluoroethylene reaction kettle, reacting for 120min at 60 ℃, washing a product obtained by the reaction with absolute ethyl alcohol for 5 times, and carrying out vacuum drying at 60 ℃ to obtain the magnetic graphene-based MOFs hybrid membrane.
The application of the prepared magnetic graphene-based MOFs hybrid membrane is used for adsorbing and removing trace phenolic endocrine disruptors in a water environment, and the specific method comprises the following steps: preparing a phenolic endocrine disruptor water sample with the pH value of 7, adding the magnetic graphene-based MOFs hybrid membrane into the water sample for oscillation adsorption, enriching with an external magnet in the process, and evaluating the adsorption efficiency of the hybrid membrane material on the basis of considering temperature, adsorption time, substrate concentration influence factors and repeated utilization rate.
The invention has the advantages that: the preparation method of the magnetic graphene-based MOFs hybrid membrane provided by the invention has the advantages of reasonable process and easiness in implementation; the magnetic graphene-based MOFs hybrid membrane prepared by the method has good chemical stability and reusability when being used for removing endocrine disruptors, has strong magnetic responsiveness in a magnetic field, and can be easily separated under the action of an external magnetic field after the 'active' adsorption and identification of phenolic endocrine disruptors are completed, so that the purposes of active identification and convenient separation are achieved; the preparation method has strong magnetic responsiveness, presettability, identifiability and practicability, brings great convenience to the removal of the phenolic endocrine disruptors, greatly improves the use efficiency of the MOFs hybrid membrane, and widens the application range of the MOFs hybrid membrane.
Drawings
Fig. 1 is an electron microscope image of a magnetic graphene material.
Fig. 2 is an electron microscope image of ZnO-modified magnetic graphene.
FIG. 3 is an electron microscope image of a magnetic graphene-based MOFs hybrid film.
Fig. 4 is an adsorption time curve of the magnetic graphene-based MOFs hybrid film.
Detailed Description
Example (b):
a preparation method of a magnetic graphene-based MOFs hybrid film comprises the following steps of firstly preparing a magnetic graphene material by a hydrothermal reduction method, then loading ZnO on the surface of the magnetic graphene material, and synthesizing the magnetic graphene-based MOFs hybrid film by in-situ growth by taking the ZnO as a metal source, wherein the preparation method comprises the following steps:
1) preparation of magnetic graphene material
The method for synthesizing the magnetic graphene material by adopting a hydrothermal method comprises the following specific steps: dissolving 1.62g of ferric chloride hexahydrate in 40mL of mixed solution of ethylene glycol and diethylene glycol, performing ultrasonic treatment for 10min, adding 100mg of graphene oxide into the uniformly mixed solution, uniformly mixing the graphene oxide and the uniformly mixed solution, then adding 0.3529g of sodium citrate and 4.32g of anhydrous sodium acetate, performing ultrasonic treatment for dissolving, and performing magnetic stirring for 30 min. And (4) putting the mixed solution into a reaction kettle, and reacting for 12 hours at 200 ℃ (taking out after natural cooling). Washing the product obtained by the reaction with absolute ethyl alcohol for 5 times, and then drying in vacuum at 60 ℃ to obtain the magnetic graphene.
Fig. 1 is an electron microscope image of a magnetic graphene material. The figure shows that: the graphene has a uniform sheet-like structure and has good light transmittance. The surface of the flaky structure is loaded with a large amount of Fe3O4The magnetic microsphere has uniform particle size of about 300 nm.
2) Preparation of ZnO modified magnetic graphene
Respectively dissolving 50mg of magnetic graphene and zinc oxide in 30mL of absolute ethyl alcohol and 20mL of absolute ethyl alcohol, performing ultrasonic treatment for 120min, slowly dropping the zinc oxide subjected to ultrasonic treatment into the absolute ethyl alcohol dispersion liquid of the magnetic graphene, performing ultrasonic treatment for 60min, washing the product for 5 times with the absolute ethyl alcohol, performing magnetic separation on the product, and performing vacuum drying at 60 ℃ to obtain the ZnO modified magnetic graphene.
Fig. 2 is an electron microscope image of ZnO-modified magnetic graphene. The following are shown in the figure: compared with the graph in fig. 1, a layer of relatively uniform nano-particles with the size of about 20nm zno is uniformly dispersed on the surface of the magnetic graphene material through electrostatic deposition in the experimental process.
3) Preparation of magnetic graphene-based MOFs hybrid membrane
10mg of ZnO-modified magnetic graphene and 80mg of dimethylimidazole were dissolved in 13.5mL of DMF and 2.5mL of H2And (4) carrying out ultrasonic treatment on the mixed solution in the O for 1 h. Putting the mixed solution after ultrasonic treatment intoAnd (3) reacting for 2 hours at the temperature of 60 ℃ in a polytetrafluoroethylene reaction kettle. Washing the product obtained by the reaction with absolute ethyl alcohol for 5 times, and then carrying out vacuum drying at 60 ℃ to obtain the magnetic graphene-based MOFs hybrid membrane.
FIG. 3 is an electron microscope image of a magnetic graphene-based MOFs hybrid film. The figure shows that: by using dimethyl imidazole and benzimidazole as etching agents, ZnO nanoparticles on the surface of ZnO modified magnetic graphene grow in situ and are converted into a layer of MOFs film, and the MOFs film is uniformly coated on the surface of microspheres in the magnetic graphene structure.
The prepared magnetic graphene-based MOFs hybrid membrane is applied to adsorption and removal of trace phenolic endocrine disruptors in a water environment, bisphenol A is taken as a target molecule, and the magnetic graphene-based MOFs hybrid membrane is used for carrying out an adsorption performance experiment on the bisphenol A:
preparing bisphenol A solution with concentration of 0.01-0.15mmol/L, adjusting pH to 7.0, respectively taking 5ml of bisphenol A solution with different concentrations, adding 5mg of magnetic graphene-based MOFs hybrid membrane, oscillating in a shaking table for 40min, separating with external magnet, respectively taking supernatant and bisphenol A solution before adsorption, and measuring absorbance value at 286nm with an ultraviolet spectrophotometer. The detection result shows that: after the magnetic graphene-based MOFs hybrid membrane material is adsorbed, the absorbance value of the supernatant at 286nm is greatly reduced compared with that of the bisphenol A solution before adsorption, and is less than 20% of that of the bisphenol A solution before adsorption, and the adsorption efficiency of the magnetic graphene-based MOFs hybrid membrane on the bisphenol A can reach 93%.
Detection of bisphenol a in tap water:
the method is to inject 5mL of 2mol/L bisphenol A solution into a 100mL volumetric flask and add tap water to obtain an actual water sample of bisphenol A. Taking 5mL of an actual water sample, adding 5mg of a magnetic graphene-based MOFs hybrid membrane, oscillating and adsorbing for 40min, separating by an external magnet, and respectively taking a supernatant and a bisphenol A solution before adsorption at 286nm and measuring the absorbance value of the solution by using an ultraviolet spectrophotometer. The detection result shows that: the adsorption efficiency of the magnetic graphene-based MOFs hybrid membrane on bisphenol A in an actual water sample can reach 72%.
FIG. 4 is a graph of the adsorption time of the magnetic graphene-based MOFs hybrid film. The figure shows that: the adsorption efficiency of the magnetic graphene-based MOFs hybrid membrane on bisphenol A is obviously higher than that of magnetic graphene, the adsorption efficiency is rapidly increased in the first 15min, and the adsorption gradually tends to be balanced after 15 min.

Claims (7)

1. The preparation method of the magnetic graphene-based MOFs hybrid membrane is characterized by comprising the following steps of: firstly, loading Fe on the surface of graphene by a hydrothermal method3O4And (2) magnetic microspheres, then loading ZnO on the surface of the magnetic microspheres by taking the magnetic graphene as a carrier to obtain ZnO modified magnetic graphene, and synthesizing the magnetic graphene-based MOFs hybrid film by utilizing a solvent etching effect and taking the ZnO as a metal source through in-situ growth.
2. The preparation method of the magnetic graphene-based MOFs hybrid film according to claim 1, wherein: the magnetic graphene material is obtained by the following method that ferric chloride hexahydrate is dissolved in a mixed solution of ethylene glycol and diethylene glycol, graphene oxide is added and uniformly mixed after ultrasonic treatment, sodium citrate and anhydrous sodium acetate are added for ultrasonic dissolution, and the mixed solution is subjected to high-temperature reaction, washing and drying.
3. The preparation method of the magnetic graphene-based MOFs hybrid film according to claim 1, wherein: the ZnO modified magnetic graphene is obtained by the following method that a magnetic graphene material and zinc oxide are respectively dissolved in absolute ethyl alcohol, the zinc oxide is dripped into absolute ethyl alcohol dispersion liquid of the magnetic graphene material after ultrasonic treatment, and the magnetic graphene material is obtained by ultrasonic treatment, washing, magnetic separation of a product and drying.
4. The preparation method of the magnetic graphene-based MOFs hybrid film according to claim 1, wherein: the magnetic graphene-based MOFs hybrid membrane is obtained by dissolving ZnO-modified magnetic graphene and dimethyl imidazole in DMF (dimethyl formamide) and H (hydrogen peroxide)2And in the mixed solution of O, reacting the mixed solution after ultrasonic treatment to obtain a product, washing and drying to obtain the magnetic graphene-based MOFs hybrid membrane.
5. The preparation method of the magnetic graphene-based MOFs hybrid film according to claim 1, wherein: the method comprises the following steps:
1) preparation of magnetic graphene material
Dissolving 1.62g of ferric chloride hexahydrate in 40mL of a mixed solution of ethylene glycol and diethylene glycol, performing ultrasonic treatment for 10min, adding 50-200 mg of graphene oxide into the uniformly mixed solution, uniformly mixing the graphene oxide and the uniformly mixed solution, adding 0.3529g of sodium citrate and 4.32g of anhydrous sodium acetate, performing ultrasonic dissolution, simultaneously performing magnetic stirring for 30min, putting the mixed solution into a reaction kettle, reacting for 12h at 200 ℃, naturally cooling, taking out, washing a product obtained by the reaction with anhydrous ethanol for 5 times, and performing vacuum drying at 60 ℃ to obtain magnetic graphene;
2) preparation of ZnO modified magnetic graphene
Respectively dissolving 50-100 mg of magnetic graphene material and 20-50 mg of zinc oxide in absolute ethyl alcohol, carrying out ultrasonic treatment for 120min, slowly dropping the zinc oxide subjected to ultrasonic treatment into the absolute ethyl alcohol dispersion liquid of the magnetic graphene material, carrying out ultrasonic treatment for 60min, washing the product for 5 times with absolute ethyl alcohol, carrying out magnetic separation on the product, and carrying out vacuum drying at 60 ℃ to obtain ZnO modified magnetic graphene;
3) preparation of magnetic graphene-based MOFs hybrid membrane
Dissolving 10-30 mg of ZnO modified magnetic graphene and 50-100 mg of dimethyl imidazole in 13.5mL of DMF and 2.5mL of H2And (3) carrying out ultrasonic treatment on the mixed solution in the O for 60min, putting the mixed solution after ultrasonic treatment into a polytetrafluoroethylene reaction kettle, reacting for 120min at 60 ℃, washing a product obtained by the reaction with absolute ethyl alcohol for 5 times, and carrying out vacuum drying at 60 ℃ to obtain the magnetic graphene-based MOFs hybrid membrane.
6. Use of a magnetic graphene-based MOFs hybrid film prepared by any one of the methods of claims 1-5, characterized in that: the method is used for adsorbing and removing trace phenolic endocrine disruptors in the water environment.
7. The use of the magnetic graphene-based MOFs hybrid film according to claim 6, wherein: preparing a practical water sample of the phenol endocrine disruptors with the pH value of 7, adding the magnetic graphene-based MOFs hybrid membrane into the water sample for oscillation and adsorption, enriching the external magnet in the process, and evaluating the adsorption efficiency of the magnetic graphene-based MOFs hybrid membrane on the basis of considering temperature, adsorption time, substrate concentration influence factors and repeated utilization rate.
CN202210323163.8A 2022-03-30 2022-03-30 Preparation method of magnetic graphene-based MOFs hybrid membrane Pending CN114682100A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210323163.8A CN114682100A (en) 2022-03-30 2022-03-30 Preparation method of magnetic graphene-based MOFs hybrid membrane

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210323163.8A CN114682100A (en) 2022-03-30 2022-03-30 Preparation method of magnetic graphene-based MOFs hybrid membrane

Publications (1)

Publication Number Publication Date
CN114682100A true CN114682100A (en) 2022-07-01

Family

ID=82140776

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210323163.8A Pending CN114682100A (en) 2022-03-30 2022-03-30 Preparation method of magnetic graphene-based MOFs hybrid membrane

Country Status (1)

Country Link
CN (1) CN114682100A (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106140094A (en) * 2016-07-04 2016-11-23 复旦大学 The synthetic method of the magnetic graphene composite that metallic organic framework is modified and application
CN108502964A (en) * 2016-01-07 2018-09-07 南京医科大学 A kind of preparation method of magnetic nanometer composite material
US20210060522A1 (en) * 2018-01-08 2021-03-04 Virginia Commonwealth University Graphene-based materials for the efficient removal of pollutants from water

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108502964A (en) * 2016-01-07 2018-09-07 南京医科大学 A kind of preparation method of magnetic nanometer composite material
CN106140094A (en) * 2016-07-04 2016-11-23 复旦大学 The synthetic method of the magnetic graphene composite that metallic organic framework is modified and application
US20210060522A1 (en) * 2018-01-08 2021-03-04 Virginia Commonwealth University Graphene-based materials for the efficient removal of pollutants from water

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
雷蕊: "MG@ZIFs基双酚A分子印迹电化学传感器的研究", 中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑, no. 1, pages 014 - 919 *

Similar Documents

Publication Publication Date Title
Ma et al. Gold nanoparticles supported by amino groups on the surface of magnetite microspheres for the catalytic reduction of 4-nitrophenol
Minale et al. Application of graphene-based materials for removal of tetracyclines using adsorption and photocatalytic-degradation: A review
Li et al. Er-doped g-C3N4 for photodegradation of tetracycline and tylosin: high photocatalytic activity and low leaching toxicity
Pan et al. Construction of nanodiamonds/UiO-66-NH2 heterojunction for boosted visible-light photocatalytic degradation of antibiotics
Beheshtkhoo et al. Green synthesis of iron oxide nanoparticles by aqueous leaf extract of Daphne mezereum as a novel dye removing material
Ahsan et al. Fe nanoparticles encapsulated in MOF-derived carbon for the reduction of 4-nitrophenol and methyl orange in water
Mahamallik et al. Tetracycline degradation in aquatic environment by highly porous MnO2 nanosheet assembly
Zhang et al. Preparation of flower-like Co3O4 QDs/Bi2WO6 pn heterojunction photocatalyst and its degradation mechanism of efficient visible-light-driven photocatalytic tetracycline antibiotics
Wu et al. Bimetallic silver/bismuth-MOFs derived strategy for Ag/AgCl/BiOCl composite with extraordinary visible light-driven photocatalytic activity towards tetracycline
CN107951902B (en) Graphene antibacterial composition and sanitary material using same
Pan et al. Nanodiamond decorated 2D hexagonal Fe 2 O 3 nanosheets with a Z-scheme photogenerated electron transfer path for enhanced photocatalytic activity
Dong et al. Synthesis and characterization of Ag/Bi 2 WO 6/GO composite for the fast degradation of tylosin under visible light
Qiu et al. Bismuth molybdate photocatalyst for the efficient photocatalytic degradation of tetracycline in water under visible-light irradiation
CN105688992A (en) Ag/Fe3O4/nano-cellulose tri-element composite material and preparation method thereof
Zhang et al. Boron nitride quantum dots decorated MIL-100 (Fe) for boosting the photo-generated charge separation in photocatalytic refractory antibiotics removal
Chen et al. ZnO nanorods/Fe 3 O 4-graphene oxide/metal-organic framework nanocomposite: recyclable and robust photocatalyst for degradation of pharmaceutical pollutants
Altin CuO-TiO2/graphene ternary nanocomposite for highly efficient visible-light-driven photocatalytic degradation of bisphenol A
CN112403268A (en) Self-cleaning Ti3C2TxPreparation method of hydrophilic flexible nanofiltration membrane, prepared filter membrane and application thereof
Ranjith et al. Highly selective surface adsorption-induced efficient photodegradation of cationic dyes on hierarchical ZnO nanorod-decorated hydrolyzed PIM-1 nanofibrous webs
Zhang et al. Synergistic adsorption of Pb (II) ions by Fe3O4 nanoparticles-decorated porous BN nanofibers
Wang et al. Fe-complex modified cellulose acetate composite membrane with excellent photo-Fenton catalytic activity
CN101352684A (en) Process for synthesizing iron-nickel alloy nano particle catalyst for selective hydrogenation
Liu et al. One-pot in situ microwave hydrothermally grown zeolitic imidazolate framework-8 on ZnIn-layered double oxides toward enhanced methylene blue photodegradation
Zhao et al. TEMPO-oxidized cellulose beads embedded with Au-doped TiO2 nanoparticles for photocatalytic degradation of Tylosin
Wang et al. Construction of activated biochar/Bi2WO6 and/Bi2MoO6 composites to enhance adsorption and photocatalysis performance for efficient application in the removal of pollutants and disinfection

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20220701

WD01 Invention patent application deemed withdrawn after publication