CN109482071B - Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane - Google Patents

Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane Download PDF

Info

Publication number
CN109482071B
CN109482071B CN201811363842.8A CN201811363842A CN109482071B CN 109482071 B CN109482071 B CN 109482071B CN 201811363842 A CN201811363842 A CN 201811363842A CN 109482071 B CN109482071 B CN 109482071B
Authority
CN
China
Prior art keywords
pvdf
composite membrane
pda
membrane
hnts
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.)
Active
Application number
CN201811363842.8A
Other languages
Chinese (zh)
Other versions
CN109482071A (en
Inventor
王倩倩
崔久云
谢阿田
刘思玮
闫永胜
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.)
Jiangsu University
Original Assignee
Jiangsu 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 Jiangsu University filed Critical Jiangsu University
Priority to CN201811363842.8A priority Critical patent/CN109482071B/en
Publication of CN109482071A publication Critical patent/CN109482071A/en
Application granted granted Critical
Publication of CN109482071B publication Critical patent/CN109482071B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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
    • B01D69/12Composite membranes; Ultra-thin membranes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D17/00Separation of liquids, not provided for elsewhere, e.g. by thermal diffusion
    • B01D17/02Separation of non-miscible liquids
    • B01D17/0202Separation of non-miscible liquids by ab- or adsorption
    • 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
    • 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
    • B01D71/30Polyalkenyl halides
    • B01D71/32Polyalkenyl halides containing fluorine atoms
    • B01D71/34Polyvinylidene fluoride
    • 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
    • C02F1/40Devices for separating or removing fatty or oily substances or similar floating material
    • 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
    • B01D2325/36Hydrophilic membranes

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Water Supply & Treatment (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Thermal Sciences (AREA)
  • Manufacturing & Machinery (AREA)
  • Physics & Mathematics (AREA)
  • Analytical Chemistry (AREA)
  • Manufacture Of Macromolecular Shaped Articles (AREA)

Abstract

The invention belongs to the technical field of preparation of environment functional materials, and particularly relates to a preparation method of a PVDF/GO @ PDA @ HNTs composite membrane; the method comprises the following specific steps: firstly, preparing and obtaining a PVDF/GO composite membrane; preparing a dopamine solution, dissolving halloysite in the dopamine solution, adding a PVDF/GO composite membrane, carrying out a shaking reaction, washing with deionized water and ethanol, and drying to prepare a PVDFGO @ PDA @ HNTs composite membrane; the invention adopts the membrane separation technology, has short flow, easy operation control, resource saving and no secondary pollution, conforms to the green chemical concept and is suitable for wide popularization and use.

Description

Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane
Technical Field
The invention belongs to the technical field of preparation of environment functional materials, and particularly relates to a preparation method and application of a PVDF/GO @ PDA @ HNTs composite membrane.
Background
In recent years, a great deal of oily wastewater caused by crude oil exploitation, offshore oil leakage accidents, domestic sewage and the like becomes a great challenge to the environment. The oily wastewater can cause great harm to the environment, for example, petroleum floats on the sea surface, and rapidly diffuses to form an airtight oil film to block the reoxygenation of the water body, so that the oxygen deficiency of the marine water body is caused, the growth of marine plankton is influenced, and the ecological balance of the sea is damaged. The oily sewage is also extremely difficult to treat, the efficiency is low, the cost is high, and the oil in the sewage is divided into four types according to the physical state: free oil, dispersed oil, emulsified oil and dissolved oil.
The membrane separation method is commonly used at present, and has the advantages of low energy consumption, high single-stage separation efficiency, flexible and simple process, low environmental pollution, strong universality and the like; however, the efficiency of membrane separation applications is limited by inherent factors such as membrane fouling resistance, thermal stability, chemical stability, etc., and by extrinsic factors such as membrane module form, operating conditions, etc. With the development of material science, the research and development of surface materials based on special wettability are rapid in recent years, the surface materials mainly comprise super-hydrophilic, super-hydrophobic, super-oleophilic, super-oleophobic, super-amphiphobic, super-amphiphilic surfaces and the like, and a series of applications are achieved in the aspects of self-cleaning surfaces, anti-fog coatings, anti-fouling coatings, anti-fingerprint coatings, micro-droplet transfer technologies, oil-water separation and the like. The polyvinylidene fluoride (PVDF) film has excellent performances of good chemical stability, high mechanical strength, high toughness and the like, and has good application prospect in the field of wastewater oil removal; however, the hydrophobic PVDF membrane has the problems of low surface energy, small permeation flux, easy pollution and the like, and the application of the PVDF membrane in the field of membrane separation is restricted.
The essence of oil-water separation is the interface problem, and the super-oleophobic or super-hydrophobic separation material is obtained by designing the special wettability of the surface of the material, which is undoubtedly the most effective means for improving the oil-water separation performance; however, the application of the membrane material based on the special wettability has many problems, such as poor swelling resistance, poor chemical resistance, fast flux attenuation, limited types of treating oily sewage, low separation efficiency, and the like, and the problems need to be solved urgently.
Disclosure of Invention
In view of the above-mentioned deficiencies in the prior art, the present invention is directed to solving one of the problems; the preparation method of the halloysite-modified super-hydrophilic/underwater super-oleophobic polyvinylidene fluoride/graphene oxide composite membrane comprises the following specific steps:
(1) preparing a vinylidene fluoride/graphene oxide blend membrane: dissolving Graphene Oxide (GO) and polyvinylidene fluoride (PVDF) powder, polyvinyl alcohol (PVA) and polyvinylpyrrolidone (PVP) into N-methyl pyrrolidone (NMP), mechanically stirring to obtain a casting solution, uniformly coating the casting solution on a glass plate, and putting the glass plate into deionized water to prepare a PVDF/GO membrane;
(2) firstly, preparing a dopamine hydrochloride solution, then dissolving Halloysite (HNTs) in the dopamine hydrochloride solution, adding the PVDF/GO membrane obtained in the step (1), and carrying out sealed oscillation reaction to obtain the PVDF/GO @ PDA @ HNTs composite membrane.
Further, in the step (1), the dosage ratio of the graphene oxide to the polyvinylidene fluoride to the polyvinyl alcohol to the polyvinylpyrrolidone to the N-methylpyrrolidone is 0.15-0.6 g: 1.5-6 g: 0.25-1 g, 0.1-0.4: 30 mL.
Further, the temperature of the mechanical stirring in the step (1) is 50 ℃, and the mechanical stirring time is 24 hours.
Further, the concentration of the dopamine hydrochloride solution in the step (2) is 2 mg/L.
Further, the dosage ratio of the halloysite to the dopamine hydrochloride solution in the step (2) is 0.05-0.2 g: 100 mL.
Further, the oscillation reaction time in the step (2) is 6-24 hours.
The super-hydrophilic composite membrane has super-hydrophilic/underwater super-oleophobic property, is strong in stability and simple to prepare, and has potential applications, such as the application in the aspects of separating oil stains in oily sewage, purifying water and the like.
Has the advantages that:
(1) the PVDF material used in the invention has low price and wide source, and the preparation method of the film is simple and has low energy consumption, thus being capable of producing PVDF film in large scale and being applied to the field of film separation.
(2) According to the invention, a dopamine bionic adhesion technology is utilized, natural mineral halloysite is loaded on a PVDF/GO membrane through a one-step method, the defect that inorganic nanoparticles loaded on the PVDF/GO membrane by a conventional suction filtration method are easy to fall off is overcome, and a PVDF/GO @ PDA @ HNTs composite membrane is prepared; through a contact angle test, the contact angle on water of the composite membrane is close to 0 degree, the contact angle under water is 153 degrees, and the composite membrane has super-hydrophilic/super-oleophobic performance under water; for the prepared PVDF @ PDA @ NiCo2(OH)6The composite membrane is subjected to various oil-water emulsion separation experiments, and the separation efficiency can reach 99.5 percent only under the gravity condition. And after 10 cycles of experimentThen, the flux recovery ratio reaches 87%, which shows that the composite membrane has good reproducibility and dirt resistance; and the filtered scanning electron microscope image shows that the halloysite nanoparticles are still firmly connected to the surface of the membrane, which shows that the composite membrane has stable structure and can effectively separate sewage.
(3) The invention adopts the membrane separation technology, has short flow, easy operation control, resource saving and no secondary pollution, conforms to the green chemical concept and is suitable for wide popularization and use.
Drawings
FIG. 1 is a scanning electron microscope image of a PVDF/GO @ PDA @ HNTs composite membrane.
FIG. 2 is a photograph of the oil contact angle of a PVDF/GO membrane.
FIG. 3 is a photograph of the oil contact angle of a PVDF/GO @ PDA @ HNTs film.
FIG. 4 is a photograph of the contact angle on water of a PVDF/GO membrane.
FIG. 5 is a photograph of the contact angle on water of PVDF/GO @ PDA @ HNTs film.
FIG. 6 is a graph of pure water flux and petroleum ether/water emulsion flux under gravity alone for PVDF/GO membrane and PVDF/GO @ PDA @ HNTs composite membranes prepared with different amounts of halloysite.
FIG. 7 is a graph of the separation efficiency of petroleum ether/water emulsion under gravity alone for PVDF/GO membrane and PVDF/GO @ PDA @ HNTs composite membranes prepared with different amounts of halloysite.
FIG. 8 is a graph of the separation efficiency of PVDF/GO @ PDA @ HNTs composite membrane for separating various oil-water emulsions.
FIG. 9 is a scanning electron microscope image after the PVDF/GO @ PDA @ HNTs composite membrane flux.
FIG. 10 is a graph of the cycling flux recovery ratio for PVDF/GO membrane and PVDF/GO @ PDA @ HNTs composite membrane.
Detailed Description
The invention is further described below with reference to specific examples:
example 1:
(1) preparation of PVDF/GO membranes: weighing 0.15g of graphene, 1.5g of polyvinylidene fluoride powder, 0.25g of polyvinyl alcohol and 0.1g of polyvinylpyrrolidone, adding the mixture into 30mL of N-methylpyrrolidone, mechanically stirring the mixture at 50 ℃ for 24 hours to obtain a casting solution, uniformly coating the casting solution on a glass plate, and putting the glass plate into deionized water to prepare a PVDF/GO composite membrane;
(2) preparing 100mL of 2mg/L dopamine hydrochloride solution, adding 0.05g of halloysite, performing ultrasonic homogenization, adding a PVDF/GO membrane, performing sealed oscillation reaction for 6 hours, taking out the membrane, washing with deionized water, and drying to obtain the PVDF/GO @ PDA @ HNTs membrane.
Example 2:
(1) preparation of PVDF/GO membranes: weighing 0.3g of graphene, 3g of polyvinylidene fluoride powder, 0.5g of polyvinyl alcohol and 0.3g of polyvinylpyrrolidone, adding the mixture into 30mL of N-methylpyrrolidone, mechanically stirring the mixture at 50 ℃ for 24 hours to obtain a membrane casting solution, uniformly coating the membrane casting solution on a glass plate, and putting the glass plate into deionized water to prepare a PVDF/GO composite membrane;
(2) preparing 100mL of 2mg/L dopamine hydrochloride solution, adding 0.1g of halloysite, performing ultrasonic homogenization, adding a PVDF/GO membrane, performing sealed oscillation reaction for 24 hours, taking out the membrane, washing with deionized water, and drying to obtain the PVDF/GO @ PDA @ HNTs membrane.
Example 3:
(1) preparation of PVDF/GO membranes: weighing 0.6g of graphene, 6g of polyvinylidene fluoride powder, 1g of polyvinyl alcohol and 0.4g of polyvinylpyrrolidone, adding the weighed materials into 30mL of N-methylpyrrolidone, mechanically stirring the materials at 50 ℃ for 24 hours to obtain a casting solution, uniformly coating the casting solution on a glass plate, and putting the glass plate into deionized water to prepare a PVDF/GO composite membrane;
(2) preparing 100mL of 2mg/L dopamine hydrochloride solution, adding 0.2g of halloysite, uniformly performing ultrasonic treatment, adding a PVDF/GO membrane, performing sealed oscillation reaction for 18 hours, taking out the membrane, washing with deionized water, and drying to obtain the PVDF/GO @ PDA @ HNTs membrane.
FIG. 1 is a scanning electron microscope image of the super-hydrophilic PVDF/GO @ PDA @ HNTs composite membrane prepared in example 2, and it can be seen from the image that a layer of rod-shaped nanoparticles is distributed on the surface of the membrane, so that the roughness of the surface of the membrane is increased.
FIG. 2 is the oil contact angle of the PVDF/GO membrane prepared in example 2, where the oil contact angle can be seen to be 123 deg., showing the underwater oleophobic property.
FIG. 3 is the oil contact angle of the superhydrophilic PVDF/GO @ PDA @ HNTs membrane prepared in example 2, where the underwater oil contact angle is 153 ° (> 150 °), showing the superhydrophobic property under water, and it can be seen that polyenerite enhances the oleophobicity of the membrane.
Fig. 4 is an on-water contact angle of the super-hydrophilic PVDF/GO composite membrane prepared in example 2, in which it can be seen from the graph that the oil contact angle is 94 °, exhibiting a hydrophobic property.
FIG. 5 is a water contact angle of the PVDF/GO @ PDA @ HNTs composite membrane prepared in example 2, and it can be seen that the water contact angle is close to 0 degree, and the super-hydrophilic performance is shown.
FIG. 6 is a graph of pure water flux and petroleum ether/water emulsion flux under gravity alone for PVDF/GO @ PDA @ HNTs composite membranes prepared in example 2 and different amounts of halloysite (0.05g, 0.1g, 0.2 g); as can be seen from the figure, the water flux of the PVDF/GO membrane is 546L.m-2.h-1(ii) a The water flux of halloysite used in the amount of 0.05g, 0.1g and 0.2g was 808L.m-2.h-1、1492L.m-2.h-1、1095L.m-2.h-1(ii) a Oil flux for PVDF/GO membranes is 325L.m-2.h-1(ii) a The oil fluxes of halloysite used at 0.05g, 0.1g and 0.2g were 447L.m respectively-2.h-1、895L.m-2.h-1、667L.m-2.h-1(ii) a The flux of 0.1g is the largest, and the flux is reduced on the contrary because the halloysite grafted on the surface of the membrane is too much, so that the pore diameter of the surface of the membrane is blocked, and the flux of the membrane is greatly reduced.
FIG. 7 is a graph of the separation efficiency of petroleum ether/water emulsions under gravity alone for PVDF/GO @ PDA @ HNTs composite membranes prepared in example 2 and different amounts of halloysite (0.05g, 0.1g, 0.2 g); the oil-water separation efficiency of the PVDF/GO membrane under the gravity condition is 78.92%; the oil-water separation efficiency of PVDF/GO @ PDA @ HNTs films prepared by different halloysite dosages (0.05g, 0.1g and 0.2g) under the gravity condition is 93.31%, 99.75% and 99.85% respectively; is far superior to the separation efficiency of PVDF/GO membranes and conforms to the principle of green chemistry.
FIG. 8 is a graph showing the separation efficiency of PVDF/GO @ PDA @ HNTs composite membrane prepared in example 2 for separating various oil-water emulsions, oil-water emulsions without emulsifier and emulsions with emulsifierThe oil-water emulsion separation efficiency of the reagent is up to more than 99.5 percent, which shows that the prepared PVDF @ PDA @ NiCo2(OH)6The composite membrane has wide applicability.
FIG. 9 is a scanning electron microscope image of the PVDF/GO @ PDA @ HNTs composite membrane prepared in example 2 after flux, and it can be seen from the scanning image that a layer of rod-shaped nanoparticles still exists on the surface of the membrane after an oil-water separation experiment, which illustrates that the prepared PVDF/GO @ PDA @ HNTs composite membrane has a stable structure.
FIG. 10 is a graph of the cycling flux recovery ratio of the PVDF/GO membrane and the PVDF/GO @ PDA @ HNTs composite membrane prepared in example 2. After 10 times of oil-water separation experiments, the flux recovery ratio of the PVDF/GO @ PDA @ HNTs membrane still reaches 87% and is far higher than that of the PVDF/GO membrane (78%), which indicates that the PVDF/GO @ PDA @ HNTs membrane has good stain resistance and regeneration performance.
Description of the drawings: the above embodiments are only used to illustrate the present invention and do not limit the technical solutions described in the present invention; thus, while the present invention has been described in detail with reference to the foregoing embodiments, it will be understood by those skilled in the art that various changes may be made and equivalents may be substituted; all such modifications and variations are intended to be included herein within the scope of this disclosure and the present invention and protected by the following claims.

Claims (6)

1. A preparation method of a PVDF/GO @ PDA @ HNTs composite membrane is characterized by comprising the following steps:
(1) preparing a vinylidene fluoride/graphene oxide composite membrane: dissolving graphene oxide and polyvinylidene fluoride powder, polyvinyl alcohol and polyvinylpyrrolidone into N-methyl pyrrolidone, mechanically stirring to obtain a membrane casting solution, uniformly coating the membrane casting solution on a glass plate, and putting the glass plate into deionized water to prepare a PVDF/GO composite membrane; the dosage ratio of the graphene oxide to the polyvinylidene fluoride to the polyvinyl alcohol to the polyvinylpyrrolidone to the N-methylpyrrolidone is 0.15-0.6 g: 1.5-6 g: 0.25-1 g, 0.1-0.4: 30 mL;
(2) firstly, preparing a dopamine hydrochloride solution, then dissolving halloysite in the dopamine hydrochloride solution, adding the PVDF/GO composite membrane obtained in the step (1), and carrying out sealed oscillation reaction to obtain a PVDF/GO @ PDA @ HNTs composite membrane; the concentration of the dopamine hydrochloride solution is 2 mg/L.
2. The preparation method of the PVDF/GO @ PDA @ HNTs composite membrane according to claim 1, wherein the temperature of the mechanical stirring in the step (1) is 50 ℃, and the time of the mechanical stirring is 24 h.
3. The preparation method of the PVDF/GO @ PDA @ HNTs composite membrane according to claim 1, wherein the dosage ratio of the halloysite to the dopamine hydrochloride solution in the step (2) is 0.05-0.2 g: 100 mL.
4. The preparation method of the PVDF/GO @ PDA @ HNTs composite membrane according to claim 1, wherein the oscillation reaction time in the step (2) is 6-24 h.
5. The application of the PVDF/GO @ PDA @ HNTs composite membrane prepared by the method according to any one of claims 1-4 is characterized in that the PVDF/GO @ PDA @ HNTs composite membrane is specifically applied to separation and purification of water quality.
6. The use of the PVDF/GO @ PDA @ HNTs composite membrane according to claim 5, wherein the PVDF/GO @ PDA @ HNTs composite membrane is specifically applied to the separation and purification of oil stains in oil-containing wastewater.
CN201811363842.8A 2018-11-16 2018-11-16 Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane Active CN109482071B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811363842.8A CN109482071B (en) 2018-11-16 2018-11-16 Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811363842.8A CN109482071B (en) 2018-11-16 2018-11-16 Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane

Publications (2)

Publication Number Publication Date
CN109482071A CN109482071A (en) 2019-03-19
CN109482071B true CN109482071B (en) 2021-06-22

Family

ID=65695180

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811363842.8A Active CN109482071B (en) 2018-11-16 2018-11-16 Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane

Country Status (1)

Country Link
CN (1) CN109482071B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110478944A (en) * 2019-09-02 2019-11-22 兰州理工大学 The preparation method and composite membrane and purposes of multi-functional concave convex rod composite membrane
CN112588134A (en) * 2020-11-19 2021-04-02 西安科技大学 Halloysite nanotube/graphene oxide oil-water separation membrane and preparation method and application thereof
CN112844065B (en) * 2021-01-15 2023-03-14 赵梓俨 MXene composite film preparation method and MXene composite film
WO2023000606A1 (en) * 2021-07-22 2023-01-26 秦继恩 Graphene composite antibacterial masterbatch, graphene quantum dot reinforced fiber and graphene quantum dot composite film, preparation method therefor, and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010006196A2 (en) * 2008-07-10 2010-01-14 Board Of Regents, The University Of Texas System Water purification membranes with improved fouling resistance
CN103611432A (en) * 2013-12-17 2014-03-05 哈尔滨工业大学 Preparation method of polymer/graphene nano composite membrane
CN107638816A (en) * 2017-11-14 2018-01-30 安徽大学 Preparation method of dopamine-assisted dispersion graphene oxide-modified polyvinylidene fluoride ultrafiltration membrane
CN108341481A (en) * 2018-01-18 2018-07-31 同济大学 It is a kind of using discarded hollow fiber ultrafiltration membrane or microfiltration membranes as the processing method of the biologic packing material of matrix
CN108771975A (en) * 2018-06-13 2018-11-09 江苏大学 A kind of preparation method and applications of super hydrophilic/underwater superoleophobic poly-vinylidene-fluoride composite film

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010006196A2 (en) * 2008-07-10 2010-01-14 Board Of Regents, The University Of Texas System Water purification membranes with improved fouling resistance
CN103611432A (en) * 2013-12-17 2014-03-05 哈尔滨工业大学 Preparation method of polymer/graphene nano composite membrane
CN107638816A (en) * 2017-11-14 2018-01-30 安徽大学 Preparation method of dopamine-assisted dispersion graphene oxide-modified polyvinylidene fluoride ultrafiltration membrane
CN108341481A (en) * 2018-01-18 2018-07-31 同济大学 It is a kind of using discarded hollow fiber ultrafiltration membrane or microfiltration membranes as the processing method of the biologic packing material of matrix
CN108771975A (en) * 2018-06-13 2018-11-09 江苏大学 A kind of preparation method and applications of super hydrophilic/underwater superoleophobic poly-vinylidene-fluoride composite film

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
A novel reduced graphene oxide-based composite membrane prepared via a facile deposition method for multifunctional applications: oil/water separation and cationic dyes removal;Yixin Peng et al.;《Separation and Purification Technology》;20180214;第200卷;第2.3部分,摘要,图1 *

Also Published As

Publication number Publication date
CN109482071A (en) 2019-03-19

Similar Documents

Publication Publication Date Title
CN109482071B (en) Preparation method and application of PVDF/GO @ PDA @ HNTs composite membrane
CN108771975B (en) Preparation method and application of super-hydrophilic/underwater super-oleophobic polyvinylidene fluoride composite membrane
CN102974238B (en) Film surface hydrophilicity modifying method through PVA grafting by utilizing biological preparation
JP6076536B2 (en) Method for producing oil-absorbing hollow fiber porous membrane
CN108579475A (en) Inner surface hydrophilic modifying hollow-fibre membrane and its preparation method and application
CN107158959B (en) Preparation method of super-hydrophilic and underwater super-oleophobic porous composite membrane
CN102085459B (en) Preparation method of anti-pollution oil-water separation ultrafiltration membrane
CN112844067A (en) Oil-water separation ceramic membrane, preparation method and oil-water separation method
CN107158970B (en) Preparation method and application of super-hydrophilic gel composite membrane
CN104906828A (en) Foam metal-based oil slick collection material and preparation method thereof
CN112755805B (en) Underwater super-oleophobic two-dimensional nanoscale mica sheet oil-water separation membrane and preparation method and application thereof
Zhong et al. One-step nanotopography construction by polyaniline polymerization for a superhydrophobic nanofibrous membrane towards direct contact membrane distillation
CN105126647A (en) Preparation method for efficient oil-water separation composite ultrafiltration membrane
CN110721600A (en) Preparation method and application of PVDF @ PDA @ ZnO composite membrane
CN113069939B (en) Titanium dioxide modified film and preparation method thereof
CN113005775B (en) Preparation method of porous super-hydrophobic carbon fiber membrane suitable for severe environment
CN112588134A (en) Halloysite nanotube/graphene oxide oil-water separation membrane and preparation method and application thereof
CN109260764B (en) Preparation method of super-hydrophilic/underwater super-oleophobic self-cleaning tissue fiber membrane
CN107789997A (en) Dish tubular nanofiltration membrane and its preparation technology
CN109158093B (en) Preparation of loess-loaded PVDF (polyvinylidene fluoride) membrane and application of loess-loaded PVDF membrane in water body remediation
CN114471198B (en) Preparation method of non-solvent induced anti-oil stain polyethersulfone ultrafiltration membrane and coating
Cao et al. The applications of porous FO membranes and polyelectrolyte draw solution in the high‐salinity organic wastewater treatment with a hybrid forward osmosis‐membrane distillation system
CN113019160B (en) Titanium dioxide modified film and preparation method thereof
CN111893766A (en) Preparation method of multifunctional pH-responsive super-wetting material and application of multifunctional pH-responsive super-wetting material in oil-water separation
Yang et al. Analysis of research status of modified PVDF ultrafiltration membrane

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
GR01 Patent grant
GR01 Patent grant