CN114159979A - Method for preparing amphiphilic pollution-resistant reverse osmosis membrane through grafting reaction - Google Patents

Method for preparing amphiphilic pollution-resistant reverse osmosis membrane through grafting reaction Download PDF

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CN114159979A
CN114159979A CN202111229623.2A CN202111229623A CN114159979A CN 114159979 A CN114159979 A CN 114159979A CN 202111229623 A CN202111229623 A CN 202111229623A CN 114159979 A CN114159979 A CN 114159979A
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reverse osmosis
amphiphilic
osmosis membrane
membrane
preparing
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仲惟雷
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Chongqing Jingxin Membrane Environmental Protection Technology Co ltd
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    • 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
    • B01D69/125In situ manufacturing by polymerisation, polycondensation, cross-linking or chemical reaction
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/02Reverse osmosis; Hyperfiltration ; Nanofiltration
    • B01D61/027Nanofiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14Ultrafiltration; Microfiltration
    • B01D61/145Ultrafiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D65/00Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
    • B01D65/10Testing of membranes or membrane apparatus; Detecting or repairing leaks
    • 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
    • B01D67/0009Organic membrane manufacture by phase separation, sol-gel transition, evaporation or solvent quenching
    • B01D67/0016Coagulation
    • 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
    • B01D67/0081After-treatment of organic or inorganic membranes
    • B01D67/0095Drying
    • 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
    • B01D71/66Polymers having sulfur in the main chain, with or without nitrogen, oxygen or carbon only
    • B01D71/68Polysulfones; Polyethersulfones
    • 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
    • B01D2325/36Hydrophilic membranes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/38Hydrophobic membranes
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Water Supply & Treatment (AREA)
  • Nanotechnology (AREA)
  • Manufacturing & Machinery (AREA)
  • Dispersion Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The invention discloses a method for preparing an amphiphilic pollution-resistant reverse osmosis membrane by a grafting reaction, which specifically comprises the following steps: (1) scraping a polysulfone or polyether sulfone ultrafiltration membrane on a non-woven fabric by an L-S phase inversion method, and cleaning with pure water and hot water; (2) preparing a water phase solution and an oil phase solution, and adjusting the mass concentration fractions of the water phase solution and the oil phase solution to obtain a high-desalination reverse osmosis membrane; (3) preparing an amphiphilic solution, carrying out ultraviolet curing grafting reaction on the reverse osmosis membrane obtained in the step (2), and then cleaning, heating and drying; (4) and (4) drying the membrane in the step (3) to obtain the waterproof oil-resistant amphiphilic pollution-resistant composite reverse osmosis membrane. The method has the characteristics of simple operation, controllable reaction, great improvement of flux and hydrophobic and oleophobic resistance of the reverse osmosis membrane, enlargement of the application range of the reverse osmosis membrane in sewage and oil, great improvement of pollution resistance, great improvement of flow rate and the like, and is particularly suitable for the field of pollution-resistant reverse osmosis membranes.

Description

Method for preparing amphiphilic pollution-resistant reverse osmosis membrane through grafting reaction
Technical Field
The invention relates to the field of reverse osmosis membrane preparation, in particular to a method for preparing an amphiphilic pollution-resistant reverse osmosis membrane through a grafting reaction.
Background
In the early 80 s of the 20 th century, the defects of cellulose materials were overcome in the United states, and a composite polyamide membrane with high water flux and high salt interception rate was developed, so that the reverse osmosis technology was widely applied to the industrial field. The application of the method in the living fields of seawater and brackish water desalination and pure water production is developed to the environmental protection field of wastewater treatment and reuse. At present, on the one hand, water resources are lacked, and a water source with lower quality than the prior water source is required to be continuously developed and utilized; on the other hand, the pressure applied by the government environmental protection department and the public demand on high-quality drinking water require the treatment method to be updated and the treatment degree to be improved, which brings huge market potential and development space for the membrane separation technology, especially the anti-pollution reverse osmosis membrane technology;
the existing anti-pollution reverse osmosis membrane is mainly applied to the fields of brackish water desalination drinking water, sewage reuse, sea water desalination primary effluent and the like, the water quality is often between 2000ppm and 30000ppm, the water quality condition is severe, the requirement of reverse osmosis membrane inflow on water quality is high, more pretreatment processes are often required to be added in front of the reverse osmosis membrane, the economic efficiency is low, in addition, the requirement of conventional reverse osmosis membrane inflow on oil in water is high, a higher deoiling and degreasing pretreatment process procedure is required to be added, the higher oil in water can not only damage a reverse osmosis membrane polyamide layer, but also oil hydrocarbon substances are difficult to remove to influence the water quality of reverse osmosis membrane effluent, and the requirements on anti-pollution performance and desalination flow stability of the reverse osmosis membrane are increasingly outstanding.
In order to solve the problems, the traditional reverse osmosis membrane preparation method is improved, and a method for preparing an amphiphilic pollution-resistant reverse osmosis membrane through a grafting reaction is provided.
Disclosure of Invention
Aiming at the defects in the prior art, the invention provides a method for preparing an amphiphilic pollution-resistant reverse osmosis membrane by a grafting reaction, which has the characteristics of simple operation, controllable reaction, great improvement on flux and hydrophobic and oleophobic resistance of the reverse osmosis membrane, enlarged application range of the reverse osmosis membrane in sewage and oil, great improvement on pollution resistance, great flow improvement and the like, and is particularly suitable for the field of pollution-resistant reverse osmosis membranes.
In order to achieve the aim of the invention, the invention adopts the specific scheme that:
a method for preparing an amphiphilic pollution-resistant reverse osmosis membrane through a grafting reaction comprises the following steps of firstly obtaining a polysulfone ultrafiltration membrane with a non-woven fabric and polysulfone double-layer structure by adopting an L-S phase inversion method, secondly obtaining a reverse osmosis membrane with a polyamide layer through interfacial polymerization, and finally obtaining an anti-pollution nanofiltration membrane through a grafting reaction with an amphiphilic group, wherein the method specifically comprises the following steps:
(1) scraping a polysulfone or polyether sulfone ultrafiltration membrane on a non-woven fabric by an L-S phase inversion method, and cleaning with pure water and hot water;
(2) preparing a water phase solution and an oil phase solution, and adjusting the mass concentration fractions of the water phase solution and the oil phase solution to obtain a high-desalination reverse osmosis membrane;
(3) preparing an amphiphilic solution, carrying out ultraviolet curing grafting reaction on the reverse osmosis membrane obtained in the step (2), and then cleaning, heating and drying;
(4) and (4) drying the membrane in the step (3) to obtain the waterproof oil-resistant amphiphilic pollution-resistant composite reverse osmosis membrane.
Preferably, the ultrafiltration membrane used in step (1) has a molecular weight cut-off distribution of 5-12 ten thousand, and the specific step of step (1) comprises: stirring and dissolving the ultrafiltration membrane in a DMAc solvent at the temperature of 50-70 ℃ to prepare a solution, then coating the solution on a non-woven fabric, and then putting the non-woven fabric in cold water at the temperature of 9-16 ℃ to prepare a flat ultrafiltration membrane;
the concentration of the Polysulfone (PS) solution is 15-20%;
the ultrafiltration membrane material used in the step (1) is polysulfone polymer, the non-woven fabric is PET non-woven fabric, and the gram weight of the ultrafiltration membrane material is 70-120 g.
Preferably, the aqueous phase solution prepared in the step (2) comprises one or more of m-phenylenediamine, p-phenylenediamine and m-benzenetriol; the water phase mixed solution comprises one or more of DMSO, DMAc, DMF and triethylamine and a mixed solution of pure water; the oil phase solution is a mixed solution containing one or more of trimesoyl chloride (TMC), terephthaloyl chloride, m-benzenetricarboxy chloride, cyclohexane, acetonitrile, xylene, methylcyclohexane, Isopar G and Isopar E or a mixed solution containing trimethylene carbonate (TMC), ethyl acetate and cyclohexane;
in the step (2), the reaction time of the ultrafiltration membrane in the water phase is 0.5-2 minutes, and the reaction time in the oil phase is 0.5-2 minutes.
Preferably, the concentration of one or more of m-phenylenediamine, p-phenylenediamine and m-benzenetricarboxylic acid is 2-5%, the concentration of the water phase mixed solution comprises a mixed solution of one or more of DMSO, DMAc, DMF and triethylamine and pure water, the concentration is 1.5-5%, and the concentration of one or more of trimesoyl chloride (TMC), terephthaloyl chloride and m-benzenetricarboxylic acid chloride is 0.15-0.5%.
Preferably, in the step (3), the substance subjected to amphiphilic modification is an amphiphilic amino acid polypeptide, and the number of amino acid groups of the polypeptide is between 2 and 6; the polypeptide has hydrophilic amino acid and oleophobic amino acid group, and is obtained through solid phase reaction, and the end of the polypeptide has the group capable of reacting with amino and acyl chloride, and the group is subjected to curing grafting reaction under ultraviolet light and a catalyst.
Preferably, the concentration of the amphiphilic polypeptide is 0.1-0.5%, the concentration of the catalyst is 0.001-0.008%, the photocuring time is 5-10s, and the drying and crosslinking reaction time is 5-15 minutes.
Preferably, the method for preparing the amphiphilic pollution-resistant reverse osmosis membrane by the prepared composite nanofiltration membrane through one grafting reaction from inside to outside comprises a four-layer structure which is sequentially a non-woven fabric, a polysulfone ultrafiltration membrane, a polyamide layer and an amphiphilic polypeptide amino acid modified layer.
The invention has the beneficial effects that:
the method has the characteristics of simple operation, controllable reaction, great improvement of flux and hydrophobic and oleophobic resistance of the reverse osmosis membrane, enlargement of the application range of the reverse osmosis membrane in sewage and oil, great improvement of pollution resistance, great improvement of flow rate and the like, and is particularly suitable for the field of pollution-resistant reverse osmosis membranes.
Detailed Description
The present invention is further described below by way of specific examples, but the present invention is not limited to only the following examples. Variations, combinations, or substitutions of the invention, which are within the scope of the invention or the spirit, scope of the invention, will be apparent to those of skill in the art and are within the scope of the invention.
A method for preparing an amphiphilic pollution-resistant reverse osmosis membrane through a grafting reaction comprises the following steps of firstly obtaining a polysulfone ultrafiltration membrane with a non-woven fabric and polysulfone double-layer structure by adopting an L-S phase inversion method, secondly obtaining a reverse osmosis membrane with a polyamide layer through interfacial polymerization, and finally obtaining an anti-pollution nanofiltration membrane through a grafting reaction with an amphiphilic group, wherein the method specifically comprises the following steps:
(1) scraping a polysulfone or polyether sulfone ultrafiltration membrane on a non-woven fabric by an L-S phase inversion method, and cleaning with pure water and hot water;
(2) preparing a water phase solution and an oil phase solution, and adjusting the mass concentration fractions of the water phase solution and the oil phase solution to obtain a high-desalination reverse osmosis membrane;
(3) preparing an amphiphilic solution, carrying out ultraviolet curing grafting reaction on the reverse osmosis membrane obtained in the step (2), and then cleaning, heating and drying;
(4) and (4) drying the membrane in the step (3) to obtain the waterproof oil-resistant amphiphilic pollution-resistant composite reverse osmosis membrane.
The cut-off molecular weight distribution of the ultrafiltration membrane used in the step (1) is 5-12 ten thousand, and the step (1) comprises the following specific steps: stirring and dissolving the ultrafiltration membrane in a DMAc solvent at the temperature of 50-70 ℃ to prepare a solution, then coating the solution on a non-woven fabric, and then putting the non-woven fabric in cold water at the temperature of 9-16 ℃ to prepare a flat ultrafiltration membrane;
the concentration of the Polysulfone (PS) solution is 15-20%;
the ultrafiltration membrane material used in the step (1) is polysulfone polymer, the non-woven fabric is PET non-woven fabric, and the gram weight of the ultrafiltration membrane material is 70-120 g.
The aqueous phase solution prepared in the step (2) comprises one or more of m-phenylenediamine, p-phenylenediamine and m-benzenetriol; the water phase mixed solution comprises one or more of DMSO, DMAc, DMF and triethylamine and a mixed solution of pure water; the oil phase solution is a mixed solution containing one or more of trimesoyl chloride (TMC), terephthaloyl chloride, m-benzenetricarboxy chloride, cyclohexane, acetonitrile, xylene, methylcyclohexane, Isopar G and Isopar E or a mixed solution containing trimethylene carbonate (TMC), ethyl acetate and cyclohexane;
in the step (2), the reaction time of the ultrafiltration membrane in the water phase is 0.5-2 minutes, and the reaction time in the oil phase is 0.5-2 minutes.
One or more of m-phenylenediamine, p-phenylenediamine and m-phenylenediamine is 2-5% in concentration, the water phase mixed solution comprises one or more of DMSO, DMAc, DMF and triethylamine and pure water, the concentration is 1.5-5%, and one or more of trimesoyl chloride (TMC), terephthaloyl chloride and m-trimesoyl chloride is 0.15-0.5%.
In the step (3), the substance for performing amphiphilic modification is amphiphilic amino acid polypeptide, and the number of amino acid groups of the polypeptide is between 2 and 6; the polypeptide has hydrophilic amino acid and oleophobic amino acid group, and is obtained through solid phase reaction, and the end of the polypeptide has the group capable of reacting with amino and acyl chloride, and the group is subjected to curing grafting reaction under ultraviolet light and a catalyst.
The concentration of the amphiphilic polypeptide is 0.1-0.5%, the concentration of the catalyst is 0.001-0.008%, the photocuring time is 5-10s, and the drying and crosslinking reaction time is 5-15 minutes.
The method for preparing the amphiphilic pollution-resistant reverse osmosis membrane by the prepared composite nanofiltration membrane through a grafting reaction from inside to outside comprises a four-layer structure which is sequentially a non-woven fabric, a polysulfone ultrafiltration membrane, a polyamide layer and an amphiphilic polypeptide amino acid modified layer.
Example 1:
1. preparing a mixed N, N-diethylamide (DMAc) solution and polysulfone particles, heating to 60 ℃, and stirring to obtain a homogeneous solution, wherein the mass ratio of the DMAc to the polyether sulfone is 85:15, and the molecular weight of the polyether sulfone is 5-12 ten thousand;
2. and (3) extruding the mixture through a precision slit, grinding a head, and mixing the mixture with S1 to coat the mixture on non-woven fabrics, wherein the thickness of the non-woven fabrics is 80-100 mu m, and the non-woven fabrics enter a cold water tank to be solidified and formed, and the temperature of the cold water tank is 10-20 ℃.
3. Preparing 0.2-0.5% anhydrous MPD and TEA 2.0g/L in the reaction tank A, dissolving in deionized water to prepare an aqueous phase solution, immersing the ultrafiltration membrane obtained in the step 2 in the reaction tank A, and taking out and drying surface water drops;
4. preparing 0.02-0.05% TMC and cyclohexane solution in the reaction tank B, immersing the ultrafiltration membrane obtained in the step S3 in the reaction tank B, taking out the reaction tank B, drying and cleaning;
5. soaking the reverse osmosis membrane obtained in the step 4 into the amphiphilic polypeptide solution obtained by synthesis, wetting and taking out, and performing infrared drying for 2-5min to obtain a grafted reverse osmosis membrane;
comparative example 1:
comparative example no step 5 of example 1 compared to example 1;
performance test:
the reverse osmosis membranes prepared in experimental example 1 and comparative example 1 were used to perform a desalination stability test on a membrane test bed. The test table is used for measuring the water flux and the desalination rate of the membrane after operation under the test conditions that the operating pressure is 0.6Mpa, the concentration is 1000PPM bovine serum albumin + pure water solution, the solution temperature is 25 ℃, and the PH value is 6.5-7.5, and the results are shown in the table 1-2:
cumulative membrane run time Experimental example 1 salt rejection Comparative example 2 salt rejection Experimental example 1 flow rate Comparative example 2 flow rate
1h 99.08% 99.04% 28.57gfd 29.03gfd
24h 99.06% 99.07% 28.09gfd 26.43gfd
48h(2d) 99.04% 99.02% 28.34gfd 24.09gfd
96h(4d) 99.02% 98.85% 28.26gfd 21.09gfd
6d 99.02% 98.76% 28.219gfd 17.09gfd
10d 98.96% 98.69% 28.13gfd 16.09gfd
30d 98.92% 98.42% 27.32gfd 15.97gfd
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the present invention, and any modifications, equivalents and improvements made within the spirit and principle of the present invention should be included in the scope of the present invention.

Claims (7)

1. A method for preparing an amphiphilic pollution-resistant reverse osmosis membrane through a grafting reaction is characterized in that a polysulfone ultrafiltration membrane with a non-woven fabric and polysulfone double-layer structure is obtained by adopting an L-S phase inversion method, then a reverse osmosis membrane with a polyamide layer is obtained through interfacial polymerization, and then an anti-pollution nanofiltration membrane is obtained through a grafting reaction with an amphiphilic group, and specifically comprises the following steps:
(1) scraping a polysulfone or polyether sulfone ultrafiltration membrane on a non-woven fabric by an L-S phase inversion method, and cleaning with pure water and hot water;
(2) preparing a water phase solution and an oil phase solution, and adjusting the mass concentration fractions of the water phase solution and the oil phase solution to obtain a high-desalination reverse osmosis membrane;
(3) preparing an amphiphilic solution, carrying out ultraviolet curing grafting reaction on the reverse osmosis membrane obtained in the step (2), and then cleaning, heating and drying;
(4) and (4) drying the membrane in the step (3) to obtain the waterproof oil-resistant amphiphilic pollution-resistant composite reverse osmosis membrane.
2. The method for preparing the amphiphilic pollution-resistant reverse osmosis membrane by the grafting reaction according to claim 1, wherein the ultrafiltration membrane used in the step (1) has a molecular weight cut-off distribution of 5-12 ten thousand, and the step (1) comprises the following specific steps: stirring and dissolving the ultrafiltration membrane in a DMAc solvent at the temperature of 50-70 ℃ to prepare a solution, then coating the solution on a non-woven fabric, and then putting the non-woven fabric in cold water at the temperature of 9-16 ℃ to prepare a flat ultrafiltration membrane;
the concentration of the Polysulfone (PS) solution is 15-20%;
the ultrafiltration membrane material used in the step (1) is polysulfone polymer, the non-woven fabric is PET non-woven fabric, and the gram weight of the ultrafiltration membrane material is 70-120 g.
3. The method for preparing the amphiphilic fouling-resistant reverse osmosis membrane by a grafting reaction according to claim 1, wherein the aqueous solution prepared in the step (2) comprises one or more of m-phenylenediamine, p-phenylenediamine and m-benzenetriol; the water phase mixed solution comprises one or more of DMSO, DMAc, DMF and triethylamine and a mixed solution of pure water; the oil phase solution is a mixed solution containing one or more of trimesoyl chloride (TMC), terephthaloyl chloride, m-benzenetricarboxy chloride, cyclohexane, acetonitrile, xylene, methylcyclohexane, Isopar G and Isopar E or a mixed solution containing trimethylene carbonate (TMC), ethyl acetate and cyclohexane;
in the step (2), the reaction time of the ultrafiltration membrane in the water phase is 0.5-2 minutes, and the reaction time in the oil phase is 0.5-2 minutes.
4. The method for preparing an amphiphilic fouling-resistant reverse osmosis membrane according to claim 3, wherein the concentration of one or more of m-phenylenediamine, p-phenylenediamine and m-phenylenediamine is 2% -5%, the concentration of the mixed solution of water phase including one or more of DMSO, DMAc, DMF and triethylamine and pure water is 1.5% -5%, and the concentration of one or more of trimesoyl chloride (TMC), terephthaloyl chloride and m-trimesoyl chloride is 0.15% -0.5%.
5. The method for preparing the amphiphilic fouling resistant reverse osmosis membrane by grafting reaction according to claim 1, wherein in the step (3), the substance for amphiphilic modification is amphiphilic amino acid polypeptide, the number of amino acid groups of the polypeptide is 2-6; the polypeptide has hydrophilic amino acid and oleophobic amino acid group, and is obtained through solid phase reaction, and the end of the polypeptide has the group capable of reacting with amino and acyl chloride, and the group is subjected to curing grafting reaction under ultraviolet light and a catalyst.
6. The method for preparing the amphiphilic fouling resistant reverse osmosis membrane by the grafting reaction according to claim 5, wherein the amphiphilic polypeptide concentration is 0.1% -0.5%, the catalyst concentration is 0.001% -0.008%, the photocuring time is 5-10s, and the drying crosslinking reaction time is 5-15 minutes.
7. The method for preparing the amphiphilic fouling-resistant reverse osmosis membrane through the grafting reaction according to claim 1, wherein the prepared composite nanofiltration membrane comprises a four-layer structure comprising a non-woven fabric, a polysulfone ultrafiltration membrane, a polyamide layer and an amphiphilic polypeptide amino acid modified layer in sequence from inside to inside.
CN202111229623.2A 2021-10-21 2021-10-21 Method for preparing amphiphilic pollution-resistant reverse osmosis membrane through grafting reaction Pending CN114159979A (en)

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