CN114191992A - Composite nanofiltration membrane for extracting lithium from salt lake and preparation method thereof - Google Patents

Composite nanofiltration membrane for extracting lithium from salt lake and preparation method thereof Download PDF

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CN114191992A
CN114191992A CN202111578632.2A CN202111578632A CN114191992A CN 114191992 A CN114191992 A CN 114191992A CN 202111578632 A CN202111578632 A CN 202111578632A CN 114191992 A CN114191992 A CN 114191992A
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nanofiltration membrane
composite nanofiltration
preparation
salt lake
solution
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CN114191992B (en
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喻慧
路宏伟
彭博
胡群辉
廖骞
贺攀
王进
贺妍博
彭军
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Hunan Ovay Technology Co ltd
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    • 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
    • B01D67/0088Physical treatment with compounds, e.g. swelling, coating or impregnation
    • 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
    • B01D67/00Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
    • B01D67/0081After-treatment of organic or inorganic membranes
    • B01D67/0083Thermal 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
    • B01D67/0081After-treatment of organic or inorganic membranes
    • B01D67/0093Chemical modification
    • 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
    • B01D69/12Composite membranes; Ultra-thin membranes
    • 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
    • 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
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Abstract

The invention provides a composite nanofiltration membrane for extracting lithium from a salt lake and a preparation method thereof, belonging to the technical field of nanofiltration membrane preparation. Soaking a basic membrane in a water phase solution and an oil phase solution in sequence, and performing heat treatment to obtain a nascent state composite nanofiltration membrane; and then modifying by adopting post-treatment liquid to obtain the nanofiltration membrane with positive charges on the surface. The composite nanofiltration membrane has high water flux, and has the characteristics of high magnesium chloride retention rate and high lithium chloride transmittance. The composite nanofiltration membrane can improve the magnesium-lithium separation ratio and improve the separation efficiency.

Description

Composite nanofiltration membrane for extracting lithium from salt lake and preparation method thereof
Technical Field
The invention relates to the technical field of nanofiltration membrane preparation, in particular to a composite nanofiltration membrane for lithium extraction in a salt lake and a preparation method thereof.
Background
Lithium is a type of lithium ion in salt lake brine, underground brine and seawater in nature, and exists mainly in the form of solid hectorite in pegmatite such as spodumene and lepidolite. At present, lithium extraction from salt lake brine is a main source of global lithium salt production, and a nanofiltration technology becomes a novel extraction technology aiming at the exploitation of salt lakes with high magnesium-lithium ratio.
Nanofiltration membranes, which are a new type of pressure-driven membrane between RO and UF membranes, are being gradually explored and clarified to be suitable for their own application boundaries. Nanofiltration membranes are used as a novel membrane separation technology, and the separation effect is mainly determined by the pore size, the charge effect and the dielectric effect. Therefore, the salt separating agent has selective permeability to different ions, thereby realizing the salt separating effect. The charge effect is also known as the Donnan effect and when a charged group membrane is placed in a solvent containing salts, the concentration of the counter ion (the ion with a charge opposite to the fixed charge in the membrane) in the solution is greater than that in the bulk solution, while the concentration of the ion of the same name in the membrane is lower than that in the bulk solution. The Donnan potential difference thus formed prevents diffusion of the homonymous ions from the bulk solution into the membrane, and the counterions are also trapped by the membrane in order to maintain electroneutrality.
However, the nanofiltration membranes currently used in the market are generally electronegative nanofiltration membranes, and are influenced by the Donnan effect as a main factor, and can effectively separate monovalent, divalent and higher anions, but have poor effects on separating monovalent, divalent and higher cations. Therefore, the nanofiltration membrane in the market cannot efficiently separate magnesium ions and lithium ions in salt lake brine.
In conclusion, a nanofiltration membrane with electropositive surface charge and a preparation method thereof are urgently needed to solve the problems in the prior art, namely, the nanofiltration membrane with low lithium chloride rejection rate and high magnesium chloride rejection rate is produced and is applied to the separation of magnesium and lithium in salt lake brine.
Disclosure of Invention
In view of the above, the invention provides a composite nanofiltration membrane for lithium extraction from a salt lake and a preparation method thereof, the composite nanofiltration membrane has high water flux, and not only can increase the retention rate of magnesium chloride, but also can improve the transmittance of lithium chloride.
The invention aims to provide a preparation method of a composite nanofiltration membrane for extracting lithium from a salt lake, which comprises the following steps:
(1) preparing an aqueous phase solution: uniformly mixing an amine substance, a water-phase additive and deionized water to obtain a water-phase solution;
(2) preparing an oil phase solution: uniformly mixing polybasic acyl chloride and an oil phase solvent to obtain an oil phase solution;
(3) preparing a nascent state composite nanofiltration membrane: firstly, soaking a base film in an aqueous phase solution, and then soaking the base film in an oil phase solution; carrying out heat treatment on the basic membrane soaked by the oil phase solution to obtain a nascent state composite nanofiltration membrane;
(4) preparation of the post-treatment solution: mixing polyethyleneimine, a catalyst and an alcohol solvent to prepare a post-treatment solution;
(5) post-treatment modification: and (4) immersing the nascent-state composite nanofiltration membrane obtained in the step (3) into the post-treatment solution, and obtaining the composite nanofiltration membrane for extracting lithium from the salt lake after the post-treatment modification is completed.
Preferably, the amine substance in the step (1) is at least one of piperazine, 1, 6-hexamethylene diamine, 1, 4-diaminocyclohexane and m-phenylenediamine;
the water phase additive is at least one of polyethylene glycol 200, polyethylene glycol 300, polyethylene glycol 400 and polyethylene glycol 800;
the mass ratio of the amine substances, the water-phase additive and the deionized water in the water-phase solution is 0.5-3: 1-5: 92-98.5.
Preferably, the polybasic acyl chloride in the step (2) is at least one of trimesoyl chloride, phthaloyl chloride, isophthaloyl chloride, terephthaloyl chloride, 4' -biphenyldicarbonyl chloride, succinoyl chloride, glutaryl dichloride, adipoyl chloride and 1, 4-cyclohexanedicarboxylic chloride;
the oil phase solvent is at least one of n-hexane, cyclohexane and heptane;
the mass ratio of the polybasic acyl chloride to the oil phase solvent in the oil phase solution is 0.05-1: 99 to 99.95.
Preferably, the preparation method of the base film in the step (3) is as follows:
weighing polyether sulfone resin and N-methyl pyrrolidone, mixing to prepare a solution, heating and stirring for 6 hours to prepare a uniformly dispersed casting film liquid, filtering, vacuum degassing, uniformly coating on a non-woven fabric on a film scraping machine, wherein the wet film thickness is 150-170 mu m, curing to form a film to obtain the base film, and refrigerating the base film in a freezer at 5 ℃ for later use.
Preferably, the nascent composite nanofiltration membrane in the step (3) is soaked in the aqueous phase solution for 15-25 s, and then a rubber roller is adopted to remove the residual aqueous phase solution on the surface of the basic membrane; soaking the base film in the oil phase solution for 10-20 s, and then removing the residual oil phase solution on the surface of the base film by using a rubber roller.
Preferably, the heat treatment method in the step (3) is to place the base film soaked in the oil phase solution in an oven at 30-90 ℃ for 1-30 min.
Preferably, the molecular weight of the polyethyleneimine of step (4) is 600, 1800, 10000 or 20000;
the catalyst is at least one of 4-dimethylamino pyridine, triethylamine and pyridine;
the alcohol solvent is at least one of methanol, ethanol and isopropanol;
preferably, the mass ratio of the polyethyleneimine, the catalyst and the alcohol solvent in the post-treatment solution in the step (4) is 0.5-3: 0.1-0.5: 96.5 to 99.4.
Preferably, the soaking time of the nascent-state composite nanofiltration membrane in the step (4) in the post-treatment modified solution is 1-20 min.
The invention also aims to provide the composite nanofiltration membrane for extracting lithium from the salt lake, which is prepared by the method.
The invention provides a preparation method of a composite nanofiltration membrane for lithium extraction in a salt lake.
Compared with the prior art, the invention has the following beneficial effects:
(1) in the preparation process of the nascent-state composite nanofiltration membrane prepared by the invention, a large amount of unreacted-NH exists on the membrane2reacting-COCl, then carrying out post-treatment modification on the nascent composite nanofiltration membrane, adding a catalyst in the post-treatment process to improve the reaction rate of secondary amine and-COCl in polyethyleneimine, further reacting unreacted-COCl in a molecular chain with secondary amine in the polyethyleneimine, reducing the content of-COCl hydrolyzed to-COOH at the tail end of a polyamide molecular chain, and simultaneously increasing a large amount of-NH-A group. The membrane surface which is originally electronegative is converted into electropositive, and the pore diameter of the membrane is not greatly changed. The main factor of the lithium ion rejection rate is the pore size, so the lithium ion rejection rate is basically unchanged; the main influencing factor of magnesium ion rejection is the Donnan effect, because the electropositive membrane surface greatly improves the rejection of magnesium ions.
(2) According to the invention, polyethylene glycol is used as a water phase additive, the viscosity of the solution is adjusted, the interfacial polymerization rate is delayed, the water production flux of the nanofiltration membrane is improved, and the permeability of inorganic salt is not influenced, so that the retention rate of magnesium chloride is increased, the permeability of lithium chloride is increased, and the magnesium-lithium separation coefficient of lithium extracted from a salt lake is further improved.
(3) The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake is simple, short in process flow, low in cost and good in application prospect.
Detailed Description
The present invention is further illustrated by the following examples, in which the preferred embodiments and materials are shown for illustrative purposes only.
Example 1
A preparation method of a composite nanofiltration membrane for extracting lithium from a salt lake comprises the following steps:
(1) preparing an aqueous phase solution: uniformly mixing piperazine, polyethylene glycol 400 and deionized water according to the mass ratio of 1:3:96 to obtain an aqueous phase solution;
(2) preparing an oil phase solution: uniformly mixing trimesoyl chloride and n-hexane according to the mass ratio of 0.2:99.8 to obtain an oil phase solution;
(3) preparing a nascent state composite nanofiltration membrane: soaking the base membrane in the aqueous phase solution for 20s, removing the aqueous phase solution remained on the surface of the base membrane by using a rubber roller, soaking the base membrane in the oil phase solution for 15s, removing the oil phase solution remained on the surface of the base membrane by using the rubber roller, placing the base membrane soaked in the oil phase solution in a drying oven at 70 ℃, and carrying out heat treatment for 5min to obtain the nascent state composite nanofiltration membrane;
(4) preparation of the post-treatment solution: mixing polyethyleneimine with polymerization degree of 10000, triethylamine and methanol solvent according to a mass ratio of 1:0.3:98.7 mixing to prepare a post-treatment solution;
(5) post-treatment modification: and (4) immersing the nascent-state composite nanofiltration membrane obtained in the step (3) into the post-treatment solution for soaking for 15min, and obtaining the composite nanofiltration membrane for extracting lithium from the salt lake after post-treatment modification is completed.
The preparation method of the base film comprises the following steps:
75g of polyether sulfone resin (PES) and 425g of N-methylpyrrolidone (NMP) are weighed and mixed to prepare 500g of solution, and the solution is stirred for 6 hours at 70 ℃ to prepare uniformly dispersed membrane casting solution. Filtering and vacuum degassing the membrane casting solution, uniformly coating the membrane casting solution on a non-woven fabric on a membrane scraping machine, wherein the wet membrane thickness is 150 mu m, evaporating for 3s at room temperature, and then immersing in ultrapure water at 16 ℃ for gel curing to form a membrane. Then, the film was completely cured with water at normal temperature, and finally the film was washed in water at 75 ℃ for 3min to obtain a base film, and the base film was refrigerated in a freezer at 5 ℃ for use.
Example 2
The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake comprises the same steps as in example 1, wherein the amine substance in the raw material is 1, 6-hexamethylene diamine, and the other raw materials are the same as in example 1.
Example 3
The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake comprises the same steps as the example 1, wherein the amine substance in the raw material is m-phenylenediamine, and other raw materials are the same as the example 1.
Example 4
The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake comprises the same steps as the example 1, wherein the polybasic acyl chloride in the raw material is isophthaloyl dichloride, and other raw materials are the same as the example 1.
Example 5
The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake comprises the same steps as the example 1, wherein the polybasic acyl chloride substances in the raw materials are terephthaloyl chloride, and other raw materials are the same as the example 1.
Example 6
The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake comprises the same steps as the example 1, wherein the water-phase additive in the raw materials is PEG200, and other raw materials are the same as the example 1.
Example 7
The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake comprises the same steps as the example 1, wherein the water phase additive in the raw materials is PEG800, and other raw materials are the same as the example 1.
Example 8
The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake comprises the same steps as the example 1, wherein the catalyst in the raw material is 4-dimethylaminopyridine, and other raw materials are the same as the example 1.
Example 9
The preparation method of the composite nanofiltration membrane for lithium extraction in the salt lake comprises the same steps as in example 1, wherein a catalyst in a raw material is 4-dimethylaminopyridine, the mass ratio of polyethyleneimine to the catalyst to an alcohol solvent is 1:0.1:98.9, and other raw materials are the same as in example 1.
Example 10
The preparation method of the composite nanofiltration membrane for lithium extraction in the salt lake comprises the same steps as in example 1, wherein a catalyst in a raw material is 4-dimethylaminopyridine, the mass ratio of polyethyleneimine to the catalyst to an alcohol solvent is 1:0.5:98.5, and other raw materials are the same as in example 1.
Example 11
The preparation method of the composite nanofiltration membrane for lithium extraction in the salt lake comprises the same steps as in example 1, wherein a catalyst in a raw material is 4-dimethylaminopyridine, the mass ratio of polyethyleneimine to the catalyst to an alcohol solvent is 0.5:0.3:99.2, and other raw materials are the same as in example 1.
Example 12
The preparation method of the composite nanofiltration membrane for lithium extraction in the salt lake comprises the same steps as in example 1, wherein a catalyst in a raw material is 4-dimethylaminopyridine, the mass ratio of polyethyleneimine to the catalyst to an alcohol solvent is 3:0.3:96.7, and other raw materials are the same as in example 1.
Comparative example 1
A preparation method of a composite nanofiltration membrane for extracting lithium from a salt lake comprises the same raw materials and steps (1) to (3) as in example 1, and post-modification treatment is not carried out.
Comparative example 2
The raw materials and the steps of the preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake are the same as those of the example 1, and no catalyst is added into the post-treatment solution.
The nanofiltration membranes prepared in the examples 1-12 and the comparative examples 1-2 are tested on a cross-flow membrane detection table, and the test conditions are as follows: (. 1) MgCl22000ppm of aqueous solution, 70psi of operating pressure, 25 ℃ of testing temperature and 6.5-7.5 of pH value, 2000ppm of LiCl aqueous solution, 70psi of operating pressure, 25 ℃ of testing temperature and 6.5-7.5 of pH value. The results obtained are shown in table 1:
TABLE 1
Figure BDA0003426255980000061
In table 1, water flux represents the amount of water permeated per unit membrane area per unit time, and the water flux represents the performance characteristics of the composite nanofiltration membrane in terms of efficiency; transmittance is the ability to transmit a particular component; the rejection rate represents the performance characteristics of the composite nanofiltration membrane in the transmission aspect.
Comparing the data in table 1, the following results were obtained:
comparing the test result data of example 1 and comparative example 1, it can be seen that: the permeability of the composite nanofiltration membrane magnesium chloride which is lack of post-treatment modification treatment is obviously increased, namely the magnesium-lithium separation effect is poor. Therefore, the post-treatment modification treatment step has a remarkable effect of improving the magnesium-lithium separation performance of the composite nanofiltration membrane.
Comparing the test result data of example 1 and comparative example 2, it can be seen that: if the post-treatment modified solution lacks the catalyst, the transmittance of the finally prepared composite nanofiltration membrane magnesium chloride cannot be reduced to the expected effect. Therefore, the catalyst has an unexpected effect on improving the magnesium-lithium separation performance of the composite nanofiltration membrane.
The data of the test results of comparative examples 1-3 show that: the composite nanofiltration membrane prepared by using piperazine or 1, 6-hexamethylene diamine as amine substances has two performances of water flux and rejection rate which are obviously superior to those of the composite nanofiltration membrane prepared by using m-phenylenediamine.
The data of the test results of comparative examples 1, 4-5 show that: the composite nanofiltration membrane prepared by adopting trimesoyl chloride as polybasic acyl chloride has better performance in the aspect of magnesium-lithium separation than the composite nanofiltration membrane prepared by adopting isophthaloyl dichloride or terephthaloyl dichloride as polybasic acyl chloride.
The data of the test results of comparative examples 1, 6-7 show that: the composite nanofiltration membrane prepared by using PEG400 as a water phase additive has better magnesium-lithium separation performance than the composite nanofiltration membrane prepared by using PEG200 and PEG800 as water phase additives. The reason is that: in the process of preparing the nascent state composite nanofiltration membrane, the molecular size of PEG400 is suitable and the aim of reducing the reaction rate is fulfilled, PEG200 does not achieve the aim of reducing the reaction rate, and the reaction defect can be caused due to the overlarge molecular size of PEG 800.
The test result data of comparative examples 8 to 12 show that: 4-dimethylamino pyridine is used as a catalyst, and when the mass ratio of polyethyleneimine to the catalyst to the alcohol solvent is 1:0.3:98.7, 1:0.1:98.9 or 1:0.5:98.5, 0.5:0.3:99.2, and 3:0.3:96.7, the prepared composite nanofiltration membrane has excellent magnesium and lithium separation performance.
In conclusion, the composite nanofiltration membrane provided by the embodiment of the invention has a remarkable improvement effect in magnesium-lithium separation compared with a common nanofiltration membrane; the preparation steps, raw material selection and raw material proportion of the composite nanofiltration membrane related by the embodiment of the invention are creatively improved.
The foregoing is only a preferred embodiment of the present invention, and it should be noted that, for those skilled in the art, various modifications and decorations can be made without departing from the principle of the present invention, and these modifications and decorations should also be regarded as the protection scope of the present invention.

Claims (10)

1. A preparation method of a composite nanofiltration membrane for extracting lithium from a salt lake is characterized by comprising the following steps:
(1) preparing an aqueous phase solution: uniformly mixing an amine substance, a water-phase additive and deionized water to obtain a water-phase solution;
(2) preparing an oil phase solution: uniformly mixing polybasic acyl chloride and an oil phase solvent to obtain an oil phase solution;
(3) preparing a nascent state composite nanofiltration membrane: firstly, soaking a base film in an aqueous phase solution, and then soaking the base film in an oil phase solution; carrying out heat treatment on the basic membrane soaked by the oil phase solution to obtain a nascent state composite nanofiltration membrane;
(4) preparation of the post-treatment solution: mixing polyethyleneimine, a catalyst and an alcohol solvent to prepare a post-treatment solution;
(5) post-treatment modification: and (4) immersing the nascent-state composite nanofiltration membrane obtained in the step (3) into the post-treatment solution, and obtaining the composite nanofiltration membrane for extracting lithium from the salt lake after the post-treatment modification is completed.
2. The method for preparing the composite nanofiltration membrane for extracting lithium from the salt lake according to claim 1, wherein the amine substance in the step (1) is at least one of piperazine, 1, 6-hexamethylenediamine, 1, 4-diaminocyclohexane and m-phenylenediamine;
the water phase additive is at least one of polyethylene glycol 200, polyethylene glycol 300, polyethylene glycol 400 and polyethylene glycol 800;
the mass ratio of the amine substances, the water-phase additive and the deionized water in the water-phase solution is 0.5-3: 1-5: 92-98.5.
3. The method for preparing the composite nanofiltration membrane for extracting lithium from the salt lake according to claim 1, wherein the poly-acyl chloride in the step (2) is at least one of trimesoyl chloride, phthaloyl chloride, isophthaloyl chloride, terephthaloyl chloride, 4' -biphenyldicarbonyl chloride, succinyl chloride, glutaryl dichloride, adipoyl chloride and 1, 4-cyclohexanedicarbonyl chloride;
the oil phase solvent is at least one of n-hexane, cyclohexane and heptane;
the mass ratio of the polybasic acyl chloride to the oil phase solvent in the oil phase solution is 0.05-1: 99 to 99.95.
4. The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake according to claim 1, wherein the preparation method of the basic membrane in the step (3) is as follows:
weighing polyether sulfone resin and N-methyl pyrrolidone, mixing to prepare a solution, heating and stirring for 6 hours to prepare a uniformly dispersed casting film liquid, filtering, vacuum degassing, uniformly coating on a non-woven fabric on a film scraping machine, wherein the wet film thickness is 150-170 mu m, curing to form a film to obtain the base film, and refrigerating the base film in a freezer at 5 ℃ for later use.
5. The preparation method of the composite nanofiltration membrane for lithium extraction from the salt lake according to claim 1, wherein the nascent composite nanofiltration membrane in the step (3) is soaked in the aqueous solution for 15-25 s, and then a rubber roller is used for removing the residual aqueous solution on the surface of the basic membrane; soaking the base film in the oil phase solution for 10-20 s, and then removing the residual oil phase solution on the surface of the base film by using a rubber roller.
6. The preparation method of the composite nanofiltration membrane for extracting lithium from the salt lake according to claim 1, wherein the heat treatment method in the step (3) is to place the base membrane soaked in the oil phase solution in a 30-90 ℃ oven and keep the temperature for 1-30 min.
7. The method for preparing the composite nanofiltration membrane for extracting lithium from the salt lake according to claim 1, wherein the molecular weight of the polyethyleneimine obtained in the step (4) is 600, 1800, 10000 or 20000;
the catalyst is at least one of 4-dimethylamino pyridine, triethylamine and pyridine;
the alcohol solvent is at least one of methanol, ethanol and isopropanol.
8. The preparation method of the composite nanofiltration membrane for lithium extraction from the salt lake according to claim 1, wherein the mass ratio of polyethyleneimine, catalyst and alcohol solvent in the post-treatment solution in the step (4) is 0.5-3: 0.1-0.5: 96.5 to 99.4.
9. The preparation method of the composite nanofiltration membrane for lithium extraction from the salt lake according to claim 1, wherein the soaking time of the nascent state composite nanofiltration membrane in the step (4) in the post-treatment modified solution is 1-20 min.
10. A composite nanofiltration membrane for extracting lithium from a salt lake, which is characterized by being obtained by the preparation method of any one of claims 1 to 9.
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CN114864876A (en) * 2022-06-10 2022-08-05 华东理工大学 Method for hydrophilic modification of surface of manganese ion sieve electric control lithium extraction membrane electrode
CN115400604A (en) * 2022-09-06 2022-11-29 西北工业大学 Positive charge nanofiltration membrane coating for magnesium-lithium separation and preparation method thereof

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