CN106563360A - Preparation method of low-charge reverse osmosis composite film - Google Patents

Preparation method of low-charge reverse osmosis composite film Download PDF

Info

Publication number
CN106563360A
CN106563360A CN201610943710.7A CN201610943710A CN106563360A CN 106563360 A CN106563360 A CN 106563360A CN 201610943710 A CN201610943710 A CN 201610943710A CN 106563360 A CN106563360 A CN 106563360A
Authority
CN
China
Prior art keywords
reverse osmosis
osmosis composite
preparation
electric charge
low electric
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
CN201610943710.7A
Other languages
Chinese (zh)
Inventor
俞三传
徐寒姣
吕振华
刘梅红
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.)
Zhejiang Sci Tech University ZSTU
Original Assignee
Zhejiang Sci Tech University ZSTU
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 Zhejiang Sci Tech University ZSTU filed Critical Zhejiang Sci Tech University ZSTU
Priority to CN201610943710.7A priority Critical patent/CN106563360A/en
Publication of CN106563360A publication Critical patent/CN106563360A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • 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
    • B01D67/0002Organic membrane manufacture
    • B01D67/0006Organic membrane manufacture by chemical reactions
    • 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
    • B01D69/10Supported membranes; Membrane supports
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/14Membrane materials having negatively charged functional groups
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/16Membrane materials having positively charged functional groups
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/18Membrane materials having mixed charged functional groups

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The invention relates to a low-charge reverse osmosis composite film and a preparation method thereof. The low-charge reverse osmosis composite film comprises non-woven fabric, a polysulfone supporting layer and a low-charge polyamide separation layer. The technical scheme is that acyl chloride groups remaining on the surface of an aromatic polyamide reverse osmosis film during the forming early period of the aromatic polyamide reverse osmosis film and macromolecules containing active groups react, so that a low-charge protective layer is introduced on the surface of the aromatic polyamide reverse osmosis composite film in a chemical bond form. The preparation method has the advantages that chemical bonds of the polyamide separation layer and the protective layer are connected, the purpose of permanently protecting the aromatic polyamide reverse osmosis composite film is achieved, the interfacial polymerization process is not affected, and high desalinization rate of the aromatic polyamide reverse osmosis composite film is guaranteed. The low-charge reverse osmosis composite film has wide application and the preparation method is simple.

Description

A kind of preparation method of low electric charge reverse osmosis composite membrane
Technical field
The invention belongs to water-treatment technology field, and in particular to a kind of preparation method of low electric charge reverse osmosis composite membrane.
Background technology
Since the 1950's, Reid is made after reverse osmosis membrane with the homogenizing acetate fiber of 6 μ m-thicks, reverse osmosis membrane separation Technology has been widely used in the fields such as sea-water brackish water desalination, the preparation of pure water ultra-pure water, drink water purifying, Treated sewage reusing.Its In, there is height by the aromatic polyamides reverse osmosis composite membrane that interfacial polymerization is prepared from by m-diaminobenzene., pyromellitic trimethylsilyl chloride The advantages of desalination, big flux, it has also become the main product in reverse osmosiss field.But in actual use, tie including inorganic matters Dirt, biological pollution, colloid pollution have seriously restricted further should for aromatic polyamides reverse osmosis composite membrane in interior fouling membrane With.Correlational study shows that most pollutant are to adsorb deposition to film surface by electrostatic interaction or hydrophobic interaction.Therefore Prepare a kind of low electric charge, high hydrophilic reverse osmosis composite membrane and be of great significance to improving its antifouling property tool.
At present, common polyamide functional layer process for modifying surface is mainly, in existing reverse osmosis composite membrane surface physics Coating or processes for chemically crosslinked polyethylene alcohol macromole, form hydration layer and protect reverse osmosis membrane not contaminated, such as CN1213985, CN101130444 etc., but the polyvinyl alcohol protective layer adhesion deposited due to polyamide stratum disjunctum and surface is weaker, easily in reality Fall off in the running of border, the separating property even basic so as to lose antifouling property.For improve anti-pollution layer with it is anti- The adhesion of osmosis composite membrane, patent CN102228809, CN102553458 etc. at high temperature can be with polyamides using epoxide group The characteristics of active group reacts in amine layer, anti-pollution layer, polyamide stratum disjunctum are connected in the form of chemical bond, so as to effectively change The weak problem of kind anti-pollution layer cohesive force, but the method needs to prepare the aromatic polyamides reverse osmosis composite membrane that completes and enters again Row high-temperature heat treatment, easily affects microstructure or the physico-chemical property of polyamide stratum disjunctum or polysulfone supporting layer, reduces reverse osmosiss The separating property of composite membrane, such as permeation flux reduce or inorganic salt rejection rate declines etc..Additionally, patent CN102921315 then exists Polyvinyl alcohol molecule is introduced in aqueous phase solution containing polyfunctional group amine, reaction is carried out with polynary acyl chlorides and is formed after polyamide desalination layer It is chemically crosslinked again, polyamide desalination layer is chemically bound together with polyvinyl alcohol crosslinked coating, is improved poly- second The adhesive force of enol coating, but as polyvinyl alcohol is polymer-function material, polyamine can be affected to carry out boundary with polynary acyl chlorides Face is polymerized, and forms more loose polyamide desalination layer, final to limit interception capacity of the reverse osmosis composite membrane to high salinity solution.
The content of the invention
To solve above-mentioned technical problem, the present invention provides a kind of low electric charge reverse osmosis composite membrane and preparation method thereof, existing On the basis of having conventional interface polymerization to prepare aromatic polyamides reverse osmosis composite membrane, the initial stage is formed using aromatic polyamides molecule residual The acid chloride groups stayed, are reacted with the macromole containing active group, so as to not affect polyamine poly- with polynary acyl chlorides interface On the premise of conjunction, light current macromole is introduced on polyamide molecule surface in the form of chemical bond, with original polyamide molecule Low electric charge polyamide stratum disjunctum is formed together, the high desalination layer function of aramid layer had both been ensure that, realizes permanent protection virtue again The purpose of fragrant polyamide reverse osmosis composite film.
The preparation method of the low electric charge reverse osmosis composite membrane of the present invention, including non-woven fabrics, polysulfone supporting layer, low electric charge polyamides Amine stratum disjunctum, the polysulfones microporous membrane that described low electric charge polyamide stratum disjunctum is made up of non-woven fabrics and polysulfone supporting layer successively with Aqueous phase solution containing m-diaminobenzene., the organic phase solution containing pyromellitic trimethylsilyl chloride, the contact of the aqueous solution containing light current macromole, and Carry out heat treatment and be obtained.
The preparation method of the low electric charge reverse osmosis composite membrane of the present invention, the light current macromole is containing in amino, hydroxyl One or two functional groups water-soluble macromolecule.
Light current macromole described in the preparation method of the low electric charge reverse osmosis composite membrane of the present invention is polyvinyl alcohol, gathers The mixture of one or more in ethylene glycol or polyethyleneimine.
Described in the preparation method of the low electric charge reverse osmosis composite membrane of the present invention, the quality of light current macromolecular aqueous solution is dense Spend for 0.001%~1.0%.Used as more preferably selecting, the mass concentration of light current macromolecular aqueous solution is 0.1%.
The low electric charge reverse osmosis composite membrane of the present invention, described heat treatment temperature are 50 DEG C~100 DEG C.As optimum temperature Temperature is selected, and data result when heat treatment temperature is 80 DEG C is best.
Beneficial effect:
Compared with prior art:The present invention forms acyl chlorides of the initial stage in film remained on surface using aromatic polyamides reverse osmosis membrane Group, and is reacted containing the macromole of active group, so as in the form of chemical bond in aromatic polyamides reverse osmosis composite membrane Surface introduces light current macromole.On the one hand, realize that polyamide stratum disjunctum is chemical bonded with protective layer, effectively solving polyamides The weak problem of cohesive force between amine stratum disjunctum and protective layer, it is ensured that its stability in actual use, reaches permanent The purpose of protection aromatic polyamides reverse osmosis composite membrane;On the other hand, polyamine is not being affected with polynary acyl chlorides interfacial polymerization shape Into stratum disjunctum on the premise of, do not increase extra heat treatment, realize that interfacial polymerization heat treatment is same with surface functional layer heat treatment Step is carried out, and advantageously ensures that the equipment with high desalinization and easy preparative of aromatic polyamides reverse osmosis composite membrane.
Specific embodiment
Enforcement to the present invention below is illustrated;
Comparative example 1
The complex reverse osmosis membrane comprising nonwoven layer, polysulfone supporting layer and aramid layer is prepared according to a conventional method.
First by the polysulfones microporous membrane being made up of non-woven fabrics, polysulfone supporting layer water phase of the immersion containing 2.0wt% m-diaminobenzene .s In solution, the polysulfones microporous membrane being had with 0.2wt% pyromellitic trimethylsilyl chlorides are contained after the solution of excess surface is removed with rubber rollers Machine phase solution is contacted 1 minute, and heat treatment 10 minutes in 80 DEG C of baking oven, obtains polyamide reverse osmosis composite film.
Determine film surface water contact angle and Zeta potential (pH=7.0), then pressure be 225PSI, temperature be 25 DEG C, PH value is the initial desalination of test compound reverse osmosis membrane under conditions of 6.5~7.5, charging is 2000mg/l sodium-chloride water solutions Rate and water flux, acquired results are shown in Table 1.
Embodiment 1:
First by the polysulfones microporous membrane being made up of non-woven fabrics, polysulfone supporting layer water phase of the immersion containing 2.0wt% m-diaminobenzene .s In solution, the polysulfones microporous membrane being had with 0.2wt% pyromellitic trimethylsilyl chlorides are contained after the solution of excess surface is removed with rubber rollers Machine phase solution contact 1 minute, with rubber rollers remove excess surface solution after again with containing 0.1wt% polyvinyl alcohol aqueous solution Contact 1 minute, and heat treatment 10 minutes in 80 DEG C of baking oven, obtain low electric charge polyamide reverse osmosis composite film.
Determine film surface water contact angle and Zeta potential (pH=7.0), then pressure be 225PSI, temperature be 25 DEG C, PH value is the initial desalination of test compound reverse osmosis membrane under conditions of 6.5~7.5, charging is 2000mg/l sodium-chloride water solutions Rate and water flux, acquired results are shown in Table 1.
Embodiment 2:
First by the polysulfones microporous membrane being made up of non-woven fabrics, polysulfone supporting layer water phase of the immersion containing 2.0wt% m-diaminobenzene .s In solution, the polysulfones microporous membrane being had with 0.2wt% pyromellitic trimethylsilyl chlorides are contained after the solution of excess surface is removed with rubber rollers Machine phase solution contact 1 minute, with rubber rollers remove excess surface solution after again with containing 0.5wt% polyvinyl alcohol aqueous solution Contact 1 minute, and heat treatment 10 minutes in 80 DEG C of baking oven, obtain low electric charge polyamide reverse osmosis composite film.
Determine film surface water contact angle and Zeta potential (pH=7.0), then pressure be 225PSI, temperature be 25 DEG C, PH value is the initial desalination of test compound reverse osmosis membrane under conditions of 6.5~7.5, charging is 2000mg/l sodium-chloride water solutions Rate and water flux, acquired results are shown in Table 1.
Embodiment 3:
First by the polysulfones microporous membrane being made up of non-woven fabrics, polysulfone supporting layer water phase of the immersion containing 2.0wt% m-diaminobenzene .s In solution, the polysulfones microporous membrane being had with 0.2wt% pyromellitic trimethylsilyl chlorides are contained after the solution of excess surface is removed with rubber rollers Machine phase solution contact 1 minute, with rubber rollers remove excess surface solution after again with containing 0.1wt% Polyethylene Glycol aqueous solution Contact 1 minute, and heat treatment 10 minutes in 80 DEG C of baking oven, obtain low electric charge polyamide reverse osmosis composite film.
Determine film surface water contact angle and Zeta potential (pH=7.0), then pressure be 225PSI, temperature be 25 DEG C, PH value is the initial desalination of test compound reverse osmosis membrane under conditions of 6.5~7.5, charging is 2000mg/l sodium-chloride water solutions Rate and water flux, acquired results are shown in Table 1.
Embodiment 4:
First by the polysulfones microporous membrane being made up of non-woven fabrics, polysulfone supporting layer water phase of the immersion containing 2.0wt% m-diaminobenzene .s In solution, the polysulfones microporous membrane being had with 0.2wt% pyromellitic trimethylsilyl chlorides are contained after the solution of excess surface is removed with rubber rollers Machine phase solution is contacted 1 minute, removed with rubber rollers after the solution of excess surface again with it is water-soluble containing 0.1wt% polyethyleneimine Liquid is contacted 1 minute, and heat treatment 10 minutes in 80 DEG C of baking oven, obtains low electric charge polyamide reverse osmosis composite film.
Determine film surface water contact angle and Zeta potential (pH=7.0), then pressure be 225PSI, temperature be 25 DEG C, PH value is the initial desalination of test compound reverse osmosis membrane under conditions of 6.5~7.5, charging is 2000mg/l sodium-chloride water solutions Rate and water flux, acquired results are shown in Table 1.
Table 1:Composite film surface characteristic and separating property
From table 1 it follows that after introducing light current macromole, the water contact on aromatic polyamides reverse osmosis composite membrane surface There is different degrees of decline in angle, elecrtonegativity, water contact angle decline be due to introduced macromole contain abundant hydroxyl or Amino, with good hydrophilic;And after elecrtonegativity decline is then because that film surface introduces light current macromole, aromatic polyamides Reverse osmosis composite membrane surface forms uniform light current protective layer, on the one hand consumes the acid chloride groups of residual, prevent its hydrolysis and The stronger carboxyl of electronegativity is produced, the protective layer of another aspect light current can effectively shield the electronegativity of polyamide molecule, so as to Realize the preparation of low electric charge reverse osmosis composite membrane.
Additionally, electronegative fall is also relevant with the concentration and physico-chemical structure of introduced macromole, work as polyvinyl alcohol When molecular mass concentration is 0.5wt%, the reverse osmosis composite membrane surface electronegativity of preparation is 0.1wt% significantly lower than mass concentration When reverse osmosis composite membrane, this be likely due to mass concentration it is higher when, the polyvinyl alcohol molecule number in solution is more, more can hold Easily deposit to reverse osmosis composite membrane surface, form more uniform protective layer;Under identical mass concentration, prepared by polyethyleneimine The reverse osmosis composite membrane that reverse osmosis composite membrane surface electronegativity is then prepared significantly lower than polyvinyl alcohol, this is mainly due to polyethylene Imines can consume more acid chloride groups with the higher amino of a large amount of reactivities, and under the conditions of identical pH, amino Electronegativity is weaker than hydroxyl.
Comparative examples 1 and embodiment 1-4, the present invention prepare low electric charge reverse osmosis composite membrane with routine techniquess system The same superior salt rejection rate of standby complex reverse osmosis membrane.

Claims (5)

1. a kind of preparation method of low electric charge reverse osmosis composite membrane, including non-woven fabrics, polysulfone supporting layer, low electric charge polyamide separation Layer, it is characterised in that:Described low electric charge polyamide stratum disjunctum, the polysulfones microporous membrane being made up of non-woven fabrics and polysulfone supporting layer Successively with the aqueous phase solution containing m-diaminobenzene., the organic phase solution containing pyromellitic trimethylsilyl chloride, the aqueous solution containing light current macromole Contact, is placed in heat treatment in 50~100 DEG C of baking oven and obtains.
2. the preparation method of low electric charge reverse osmosis composite membrane according to claim 1, it is characterised in that:Described light current Macromole is the water-soluble macromolecule containing one or two functional groups in amino, hydroxyl.
3. the preparation method of low electric charge reverse osmosis composite membrane according to claim 1, it is characterised in that:Described light current Macromole is the mixture of one or more in polyvinyl alcohol, Polyethylene Glycol or polyethyleneimine.
4. the preparation method of low electric charge reverse osmosis composite membrane according to claim 1, it is characterised in that:The light current is big The mass concentration of molecule aqueous solution is 0.001%~1.0%.
5. the preparation method of low electric charge reverse osmosis composite membrane according to claim 4, it is characterised in that:The light current is big The mass concentration of molecule aqueous solution is 0.1%.
CN201610943710.7A 2016-11-02 2016-11-02 Preparation method of low-charge reverse osmosis composite film Pending CN106563360A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610943710.7A CN106563360A (en) 2016-11-02 2016-11-02 Preparation method of low-charge reverse osmosis composite film

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610943710.7A CN106563360A (en) 2016-11-02 2016-11-02 Preparation method of low-charge reverse osmosis composite film

Publications (1)

Publication Number Publication Date
CN106563360A true CN106563360A (en) 2017-04-19

Family

ID=58536505

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610943710.7A Pending CN106563360A (en) 2016-11-02 2016-11-02 Preparation method of low-charge reverse osmosis composite film

Country Status (1)

Country Link
CN (1) CN106563360A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107213804A (en) * 2017-07-18 2017-09-29 宁波日新恒力科技有限公司 A kind of antibacterial reverse osmosis composite membrane and its preparation method and application
CN107694357A (en) * 2017-11-22 2018-02-16 贵阳时代沃顿科技有限公司 A kind of preparation method of modified anti-pollution hydridization reverse osmosis membrane
CN109692585A (en) * 2017-10-20 2019-04-30 中国石油化工股份有限公司 Nanofiltration membrane and its preparation method and application
CN110052179A (en) * 2019-04-18 2019-07-26 万华化学集团股份有限公司 A kind of preparation method of antipollution composite nanometer filtering film
CN110201552A (en) * 2019-05-13 2019-09-06 湖北大学 With micropore/meso-hole structure nano-porous fiber film and preparation method thereof
CN113351026A (en) * 2021-05-17 2021-09-07 浙江理工大学 Preparation method of polyamide composite membrane with high controllability
CN115814609A (en) * 2022-12-05 2023-03-21 蓝星(杭州)膜工业有限公司 High-yield decolorizing membrane for treating printing and dyeing wastewater and preparation method thereof

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1989005182A1 (en) * 1987-12-02 1989-06-15 Japan Represented By Ministry Of International Tra Hydrolyzed membrane and process for its production
CN1257748A (en) * 1998-12-24 2000-06-28 中国科学院长春应用化学研究所 Alcohol-water system modifying process for inner interface of inverse osmosis membrane
CN101112675A (en) * 2006-07-27 2008-01-30 中国科学院大连化学物理研究所 Method for modifying compound film surface
WO2011088505A1 (en) * 2010-01-19 2011-07-28 Flinders University Of South Australia Low-fouling filtration membranes
CN102921315A (en) * 2012-11-02 2013-02-13 北京碧水源膜科技有限公司 Anti-pollution reverse osmosis membrane and preparation method thereof
CN103143270A (en) * 2013-03-19 2013-06-12 中国科学院长春应用化学研究所 Hydrophilic antiosmosis composite membrane and preparation method thereof
CN104190272A (en) * 2014-09-04 2014-12-10 北京碧水源膜科技有限公司 Anti-pollution composite reverse osmosis membrane and preparation method thereof
CN104815567A (en) * 2015-04-08 2015-08-05 天津大学 Reverse osmosis membrane with polyvinylamine grafted on surface, and preparation method thereof

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1989005182A1 (en) * 1987-12-02 1989-06-15 Japan Represented By Ministry Of International Tra Hydrolyzed membrane and process for its production
CN1257748A (en) * 1998-12-24 2000-06-28 中国科学院长春应用化学研究所 Alcohol-water system modifying process for inner interface of inverse osmosis membrane
CN101112675A (en) * 2006-07-27 2008-01-30 中国科学院大连化学物理研究所 Method for modifying compound film surface
WO2011088505A1 (en) * 2010-01-19 2011-07-28 Flinders University Of South Australia Low-fouling filtration membranes
CN102921315A (en) * 2012-11-02 2013-02-13 北京碧水源膜科技有限公司 Anti-pollution reverse osmosis membrane and preparation method thereof
CN103143270A (en) * 2013-03-19 2013-06-12 中国科学院长春应用化学研究所 Hydrophilic antiosmosis composite membrane and preparation method thereof
CN104190272A (en) * 2014-09-04 2014-12-10 北京碧水源膜科技有限公司 Anti-pollution composite reverse osmosis membrane and preparation method thereof
CN104815567A (en) * 2015-04-08 2015-08-05 天津大学 Reverse osmosis membrane with polyvinylamine grafted on surface, and preparation method thereof

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107213804A (en) * 2017-07-18 2017-09-29 宁波日新恒力科技有限公司 A kind of antibacterial reverse osmosis composite membrane and its preparation method and application
CN109692585A (en) * 2017-10-20 2019-04-30 中国石油化工股份有限公司 Nanofiltration membrane and its preparation method and application
CN107694357A (en) * 2017-11-22 2018-02-16 贵阳时代沃顿科技有限公司 A kind of preparation method of modified anti-pollution hydridization reverse osmosis membrane
CN107694357B (en) * 2017-11-22 2020-10-27 时代沃顿科技有限公司 Preparation method of modified pollution-resistant hybrid reverse osmosis membrane
CN110052179A (en) * 2019-04-18 2019-07-26 万华化学集团股份有限公司 A kind of preparation method of antipollution composite nanometer filtering film
CN110052179B (en) * 2019-04-18 2021-07-23 万华化学集团股份有限公司 Preparation method of anti-pollution composite nanofiltration membrane
CN110201552A (en) * 2019-05-13 2019-09-06 湖北大学 With micropore/meso-hole structure nano-porous fiber film and preparation method thereof
CN110201552B (en) * 2019-05-13 2021-07-13 湖北大学 Nano porous fiber membrane with micropore/mesopore structure and preparation method thereof
CN113351026A (en) * 2021-05-17 2021-09-07 浙江理工大学 Preparation method of polyamide composite membrane with high controllability
CN115814609A (en) * 2022-12-05 2023-03-21 蓝星(杭州)膜工业有限公司 High-yield decolorizing membrane for treating printing and dyeing wastewater and preparation method thereof
CN115814609B (en) * 2022-12-05 2023-09-26 蓝星(杭州)膜工业有限公司 High-water-yield decolorizing film for treating printing and dyeing wastewater and preparation method thereof

Similar Documents

Publication Publication Date Title
CN106563360A (en) Preparation method of low-charge reverse osmosis composite film
CN110052179B (en) Preparation method of anti-pollution composite nanofiltration membrane
CN107670513B (en) Plant polyphenol modified polymer film and preparation method and application thereof
CN105435653B (en) A kind of composite nanometer filtering film to divalent ion removing with high selectivity and preparation method thereof
US9504967B2 (en) Composite membrane with multi-layered active layer
TWI458543B (en) Method of improving performance of ultrafiltration or microfiltration membrane processes in landfill leachate treatment
CN104190272A (en) Anti-pollution composite reverse osmosis membrane and preparation method thereof
CN104781001B (en) Polyamide water process seperation film with equipment with high desalinization and high flux property and preparation method thereof
CN108325389B (en) Azlactone-based polyamide membrane and preparation method thereof
CN104190265A (en) Low-pressure high-flux chlorine-containing polymer nanofiltration membrane with stable separation layer and preparation method thereof
CN106178973B (en) A kind of energy-saving NF membrane and preparation method thereof for water cleaning systems
CN102921315B (en) Anti-pollution reverse osmosis membrane and preparation method thereof
CN105148750B (en) A kind of method that polyamide composite film surface is modified
TWI715110B (en) Vorrichtung und verfahren zur reinigung von mit elektrolyten und farbstoffen verunreinigtem abwasser
CN106582299B (en) A kind of graphene-based 3D modified by nano particles organic separation membrane preparation method of ammoxidation
CN104548952B (en) A kind of preparation method of antibacterial composite nanometer filtering film
CN110201545B (en) Preparation method of antibacterial high-flux nanofiltration membrane
WO2011136029A1 (en) Semi-permeable composite membrane
CN103785297A (en) Composite nanofiltration membrane containing organically modified attapulgite and preparation method thereof
CN101228214A (en) Method of manufacturing for aromatic polyamide composite membrane
CN104383822A (en) Polyvinyl chloride hollow fiber composite nanofiltration membrane and preparation method thereof
KR101230843B1 (en) Fouling resistance polyamide reverse osmosis membrane and manufacturing method thereof
KR101944118B1 (en) Reverse Osmosis membrane having excellent fouling resistance and manufacturing method thereof
CN102228809B (en) Method for preparing pollution-resisting reverse osmosis polyamide composite membrane
CN114345152B (en) High-flux anti-pollution composite nanofiltration membrane and preparation method thereof

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20170419

RJ01 Rejection of invention patent application after publication