CN105435653A - Composite nano filtration membrane with high selectivity on removing divalent ions and preparation method thereof - Google Patents

Composite nano filtration membrane with high selectivity on removing divalent ions and preparation method thereof Download PDF

Info

Publication number
CN105435653A
CN105435653A CN201510952929.9A CN201510952929A CN105435653A CN 105435653 A CN105435653 A CN 105435653A CN 201510952929 A CN201510952929 A CN 201510952929A CN 105435653 A CN105435653 A CN 105435653A
Authority
CN
China
Prior art keywords
layer
desalination
amine
acyl chlorides
high selectivity
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.)
Granted
Application number
CN201510952929.9A
Other languages
Chinese (zh)
Other versions
CN105435653B (en
Inventor
梁松苗
许国杨
吴宗策
蔡志奇
金焱
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.)
Wharton Technology Co Ltd
Original Assignee
Vontron Technology Co Ltd
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 Vontron Technology Co Ltd filed Critical Vontron Technology Co Ltd
Priority to CN201510952929.9A priority Critical patent/CN105435653B/en
Publication of CN105435653A publication Critical patent/CN105435653A/en
Application granted granted Critical
Publication of CN105435653B publication Critical patent/CN105435653B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

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
    • B01D71/58Other polymers having nitrogen in the main chain, with or without oxygen or carbon only
    • B01D71/60Polyamines
    • 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
    • B01D69/12Composite membranes; Ultra-thin membranes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2323/00Details relating to membrane preparation
    • B01D2323/12Specific ratios of components used

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 the technical field of nano filtration membrane and preparation thereof, and especially relates to a composite nano filtration membrane with a high selectivity on removing divalent ions and a preparation method thereof. The preparation method is characterized in that a mixedly crosslinking desalination layer and a charged grafted functional layer for enhancing ion selectivity are arranged on a polysulfone porous support layer; through the mixed crosslinking of aromatic amine and aliphatic amine, the molecular crosslinking structure of the desalination layer is adjusted, thus the crosslinking desalination layer has a unique smooth particle accumulation structure, which is better than the structure of a conventional nano filtration membrane desalination layer; and moreover, the introduced charged grafted functional layer enhances the effect of charge density and groups in ion selectivity and ion rejection. So that the sodium chloride desalination rate of the prepared composite nano filtrate membrane is less than 40%, the magnesium chloride desalination rate is more than 97%, the magnesium sulfate desalination rate is more than 98%, the calcium chloride desalination rate is more than 93%; the removal ratio of monovalent ion to divalent ion is high, the monovalent ions and divalent ions can be effectively separated, and the selective removal of divalent ions is improved.

Description

A kind of composite nanometer filtering film with high selectivity and preparation method thereof is removed to divalent ion
Technical field
The present invention relates to NF membrane and preparing technical field thereof, especially a kind of composite nanometer filtering film with high selectivity and preparation method thereof is removed to divalent ion.
Background technology
Nanofiltration is as one of pressure-driven membrane process.Because it has low energy consumption and macroion optionally feature, be widely used in that material is concentrated, sewage disposal, the field such as salt refining and medicine separation.Solute molecule or the ion transmittance process in NF membrane is usually comparatively complicated, by the control of Donnan effect, stereoeffect, dielectric effect and effect of mass transmitting.Microhydrodynamics involved by nanofiltration process and interface event usually and the charged character of solute molecule size, solute and film, membrane pore structure and residing liquid environment have close contacting.Based on the energy Si Te-Planck equation expanded, above-mentioned influence factor can carry out predicting and judging in theoretical model.The desalination layer of most NF membrane or ion select layer to have charged character, and the charged kind of institute and density are by the character of NF membrane surface or inner entrained the dissociated group of fenestra and density decision.Preparation technology's classification that the group that can dissociate then is controlled by material selected in NF membrane preparation process and acts on.Researcher generally can be with the polymeric material of the group that can dissociate if the material such as sulfonated polyether sulfone and sulfonated polyether-ether-ketone is via the preparation of phase separation casting film by choosing, and also can introduce last handling process by centering film and effectively prepare.Usually, the transfer behavior of solute in NF membrane can by designing the charged character of special film and physics pass structure comes effectively to be controlled.
Up to now, researcher have developed the multiple NF membrane technology of preparing comprising interfacial polymerization, nano combined and ultraviolet process etc.Wherein interfacial polymerization is because it is simple, controllability is got well and be applicable to the advantages such as large-scale industrial production and become one of major technique preparing composite nanometer filtering film.Composite nanometer filtering film is generally made up of ultrafiltration supporting layer and ultra-thin desalination layer.The polycondensation reaction preparation that ultra-thin desalination layer is carried out at oil phase and aqueous phase interface via two kinds of activated monomers.Its thickness is usually at 200 ~ 400nm.Participated in the monomeric species of reaction by adjustment, can flexibly effectively the charged character on controlling diaphragm top layer and other face character as stain resistance, temperature tolerance and resistance to physical damnification ability etc.Desalination layer to the water permeability of NF membrane, solute is separated and the efficiency of overall nanofiltration process has material impact.Therefore, select suitable active reaction set of monomers to merge carrying out derivatization to it is the main path developed high-performance NF membrane at present and solve membrane pollution problem.Aliphatic and aromatic amine monomer such as bisphenol-A, tannic acid, m-phenylene diamine (MPD) and polyvinylamine etc. prepare composite nanometer filter film activity desalination layer for reacting with pyromellitic trimethylsilyl chloride or dimethyl chloride.Wherein the most common and NF membrane that is large-scale commercial often adopts m-phenylene diamine (MPD) or piperazine and pyromellitic trimethylsilyl chloride to be prepared.Research shows, m-phenylene diamine (MPD) and piperazine make to there is larger difference between the NF membrane performance of corresponding preparation due to the difference of molecular structure.As piperazinyl nanofiltration is being higher than the nanofiltration of m-phenylene diamine (MPD) base in selective between divalent ion and monovalent ion, the overall salt rejection rate of m-phenylene diamine (MPD) base nanofiltration is then far above piperazinyl nanofiltration.Difference in this performance may derive from the difference of active desalination layer in dielectric property and pass structure.Difference due to monomer character causes the difference of NF membrane on filtering feature also to make the selection of film application scenario must from respective intrinsic advantage.In addition, surface grafting technology can be applied to exploitation further and design the NF membrane with better contamination resistance and bacteriostasis.Given this, the present invention plans aliphatic and aromatic amine monomer combines the contribution advantage of ion selectivity, salt rejection rate and flux separately, and introduce surface grafting technology to adjust the charged situation of desalination layer, exploitation has high flux and macroion optionally nanofiltration film.
Summary of the invention
In order to solve the above-mentioned technical problem existed in prior art, the invention provides and a kind of composite nanometer filtering film with high selectivity and preparation method thereof be removed to divalent ion.
Be achieved particular by following technical scheme:
A kind ofly divalent ion is removed to the composite nanometer filtering film with high selectivity, be made up of nonwoven layer, polysulfone porous supporting layer, crosslinked desalination layer and charged grafting functional layer, wherein, polysulfone porous supporting layer is arranged in nonwoven layer, and crosslinked desalination layer and charged grafting functional layer are successively set on polysulfone porous supporting layer; Crosslinked desalination layer is prepared at profit phase interfacial reaction by amine mixture and acyl chlorides monomer mixture; Charged grafting functional layer by chemical grafting treated in crosslinked desalination layer.
Described amine mixture is mixed by aliphatic amine and aromatic amine; Described acyl chlorides monomer mixture by the acyl chlorides monomer of the acyl chlorides monomer and three-functionality-degree with two degrees of functionality arbitrarily than mixing.
Described aliphatic amine is at least one in cyclohexanediamine, piperazine, ethylene glycol amine, ethylenediamine, propane diamine, butanediamine, hexamethylene diamine, monoethanolamine, polymine and triethylamine.
Described aromatic amine is at least one in aniline, m-phenylene diamine (MPD), p-phenylenediamine (PPD), o-phenylenediamine, terephthaldehyde's ammonia and m-xylene diamine.
Described amine mixture, its mass concentration when profit phase interfacial reaction is 1.5-5%.
Described amine mixture, fatty amines accounts for the 0.5-50% of aromatic amine weight; More excellent is 1-10%, and more excellent is 3-7%, and optimum is 5%.
Described acyl chlorides monomer mixture, its mass concentration when profit phase interfacial reaction is 0.07-0.4%; The acyl chlorides monomer of two described degrees of functionality is at least one in terephthalyl chloride, isophthaloyl chloride, phthalyl chlorine and biphenyl dimethyl chloride; Described three-functionality-degree acyl chlorides monomer is pyromellitic trimethylsilyl chloride.
Described charged grafting functional layer is reacted by amino residual in active group molecule and crosslinked desalination layer and/or acyl chlorides and/or carboxylate radical to be prepared, and its surface charge density and kind are by the kind of active group molecule and regulating and controlling of quantities.
Described active group molecule is at least containing a kind of molecule in carboxyl, acid anhydrides, epoxy radicals, acyl chlorides, sulfonic acid chloride, hydroxyl and amino.
Described the preparation method that divalent ion removes the composite nanometer filtering film with high selectivity to be comprised the following steps:
(1) prepare polysulfones casting solution after being mixed with pore former, solvent by polysulfones particle, and polysulfones casting solution is coated in nonwoven layer, and dipping is with water, obtains polysulfone porous supporting layer;
(2) fatty amines is mixed with into amine mixture with aromatic amine, acid binding agent and water, and the polysulfone porous supporting layer that step (1) obtains be impregnated in wherein, after the absorption of polysulfone porous supporting layer is saturated, take out, adopt nitrogen to remove the water droplet of remained on surface;
(3) after the acyl chlorides monomer of two degrees of functionality and the acyl chlorides monomer of three-functionality-degree being mixed into acyl chlorides monomer mixture, the polysulfone porous supporting layer that step (2) process terminates be impregnated in wherein, the crosslinked desalination layer of reaction preparation, after time to be impregnated reaches 15-25s, adopt nitrogen to remove the residual oil phase solvent of face under room temperature, the NF membrane of crosslinked desalination layer must be had;
(4) active group molecule is become after the aqueous solution with catalyst complex, again this aqueous solution be coated in the NF membrane surface with crosslinked desalination layer or the NF membrane with crosslinked desalination layer impregnated in the aqueous solution after 45-55s, be placed on 5-10min in baking oven again, obtain and the composite nanometer filtering film with high selectivity is removed to divalent ion.
Temperature in baking oven in said method is 50-80 DEG C.
Above-mentioned active group molecule is at least one in maleic anhydride, salicylic acid, benzoic acid, acetic acid, polyacrylic acid, epoxy E-51, polyethylene glycol, polyvinyl alcohol, polymine, pyromellitic trimethylsilyl chloride, monoethanolamine, triethylamine, cyclohexylamine, ethylene glycol amine, glycerine, glycerin ether, PPG, tetramethyl dipropyl support group triamine, bisphenol-A and poly (hexamethylene) hydrochloride, cyclohexane etc.
Above-mentioned active group molecule is after becoming the aqueous solution with catalyst complex, and wherein the mass concentration of active group molecule is 0.1-2%, and the mass concentration of catalyst is 0.01 ~ 1%.
Above-mentioned temperature when being coated in the NF membrane surface with crosslinked desalination layer or the NF membrane with crosslinked desalination layer being impregnated in the aqueous solution can also be 40-110 DEG C, and more excellent is 60-80 DEG C, and optimum is 70 DEG C.Processing time can also be 0.5-20min, and optimum is 3-10min.
Above-mentioned catalyst is any one in hydrochloric acid, the concentrated sulfuric acid, DMF, 1-METHYLPYRROLIDONE, oxolane or NaOH, and its mass concentration is 0.01-1%.Described acid binding agent is at least one in sodium carbonate, sodium hydrogen phosphate, NaOH and potassium hydroxide, and mass concentration is 0.01 ~ 1%.
Above-mentioned polysulfones particle and pore former, solvent, the mass ratio of its mixing is 15 ~ 21: 0.5 ~ 5: 74 ~ 84.5.Described pore former is polyvinyl alcohol.Described solvent is the one in DMF or DMA.Be immersed in pure water after described polysulfones casting solution coating.
Described aromatic amine and the addition of fatty amines make described amine mixture, and its mass concentration when profit phase interfacial reaction is 1.5-5%.Described fatty amines accounts for the 0.5-50% of aromatic amine weight; More excellent is 1-10%, and more excellent is 3-7%, and optimum is 5%; The object of acid binding agent makes pH value be 10-12.
Compared with prior art, technique effect of the present invention is embodied in:
By adopting aromatic amine and fatty amine mixing to be cross-linked, the molecule crosslinked structure of desalination layer being adjusted, making crosslinked desalination layer have unique level and smooth build-up of particles structure, being better than traditional NF membrane desalination layer structure; Combine again and introduce charged grafting layer, enhance charged density and the effect of group in ion selective retention, make the composite nanometer filtering film prepared, its to the salt rejection rate of sodium chloride lower than 40%, to the salt rejection rate of magnesium chloride higher than 97%, to the salt rejection rate of magnesium sulfate higher than 98%, to the salt rejection rate of calcium chloride higher than 93%, it is to monovalent ion and bivalent ionsly remove than having obvious superiority, effectively can be separated by monovalence divalent ion, improve bivalent ions selectively removing.
In addition, this researcher removes to divalent ion the contrast experiment that the composite nanometer filtering film with high selectivity carries out flux and different ions salt rejection rate to of the present invention in conjunction with a large amount of experiments, specific as follows:
The preparation of control sample:
(1) 20gPEG1000 is scattered in 800gN, in N-dimethylacetylamide, stirs 30min at 1600 rpm with mechanical agitator, thereafter 180g polysulfones is dispensed into wherein, and heats up, stirring and dissolving under 80 degree and 1400rpm rotating speed, dissolution time 12h.Thing to be polymerized dissolves completely, gained solution is placed in vacuum drying oven standing and defoaming, inclined heated plate 10h.Adopt slot coated station to be spread evenly across on non-woven fabrics gained solution, and solidify in the distilled water of 20 degree, setting time 4 minutes, prepared polysulfones ultrafiltration support membrane, wherein polysulfones layer thickness is 50um.
(2) be dissolved in 953g deionized water by 45g m-phenylene diamine (MPD) and 2g NaOH, stirring and dissolving obtains amine monomers solution completely.
(3) be dissolved in cyclohexane by 2.0g pyromellitic trimethylsilyl chloride, stirring and dissolving obtains solution of acid chloride.
(4) the polysulfones ultrafiltration support membrane of preparation in (1) is soaked 30s in amine aqueous solution, taking-up drains.
(5) the polysulfones ultrafiltration supporting layer having soaked amine aqueous solution in (4) is placed in solution of acid chloride and carries out interfacial reaction, reaction time 20s, preserve in deionized water after taking out the residual cyclohexane of air-dry face.
Laboratory sample:
Laboratory sample chooses product prepared by embodiment 7-embodiment 10.
Experimental technique:
Get control sample and the selective composite nanometer filtering film of embodiment of the present invention gained macroion, test its separating property, the operating condition of employing is: when testing for monovalent ion, and feed liquor is the sodium-chloride water solution of 4000mg/l; When testing for divalent ion, feed liquor is respectively the magnesium sulfate of 2000mg/l, magnesium chloride and calcium chloride water; Operating pressure is 100psi, and operating temperature is 25 DEG C, and solution ph is 6.8; And obtain salt rejection rate (R) and water flux (F) by the computing formula of salt rejection rate and water flux.Getting supporting layer is polysulfone porous membrane, and desalination layer is Wholly aromatic polyamide (m-phenylene diamine (MPD) and pyromellitic trimethylsilyl chloride), thickness be 0.18 RO film be comparative example, obtain its salt rejection rate (R) and water flux (F).Salt rejection rate and water flux are two important parameters evaluating reverse osmosis membrane, and the salt rejection rate of reverse osmosis membrane and the size of water permeation flux directly decide the efficiency of reverse osmosis process.Salt rejection rate (R) refers under certain operating conditions, feeding liquid salinity (Cf) and the difference of salinity (Cp) and the ratio of feeding liquid salinity (Cf) in penetrating fluid, and its computing formula is:
R ( % ) = C f - C p C f × 100 %
Water flux (F) is under certain operating conditions, and through the volume (V) of the water of per membrane area (A) in the unit interval (t), its unit is GFD, and its computing formula is:
F=V/At
Experimental result:
Experimental result is shown in Table 1:
Table 1
As can be seen from Table 1, within the scope of the present invention, the selective composite nanometer filtering film of the macroion of gained to monovalent ion and bivalent ions discrimination apparently higher than reference substance.
Accompanying drawing explanation
Fig. 1 is scanning electron microscope (SEM) photograph divalent ion being removed to the composite nanometer filtering film with high selectivity of the present invention.
Detailed description of the invention
Below in conjunction with concrete embodiment, further restriction is done to technical scheme of the present invention, but claimed scope is not only confined to done description.
Embodiment 1
A kind ofly divalent ion is removed to the composite nanometer filtering film with high selectivity, be made up of nonwoven layer, polysulfone porous supporting layer, crosslinked desalination layer and charged grafting functional layer, wherein, polysulfone porous supporting layer is arranged in nonwoven layer, and crosslinked desalination layer and charged grafting functional layer are successively set on polysulfone porous supporting layer; Crosslinked desalination layer is prepared at profit phase interfacial reaction by amine mixture and acyl chlorides monomer mixture; Charged grafting functional layer by chemical grafting treated in crosslinked desalination layer.Described amine mixture is mixed by aliphatic amine and aromatic amine; Described acyl chlorides monomer mixture by the acyl chlorides monomer of the acyl chlorides monomer and three-functionality-degree with two degrees of functionality arbitrarily than mixing.Described aliphatic amine is cyclohexanediamine.Described aromatic amine is aniline.Described amine mixture, its mass concentration when profit phase interfacial reaction is 1.5%.Described amine mixture, fatty amines accounts for 0.5% of aromatic amine weight; Described acyl chlorides monomer mixture, its mass concentration when profit phase interfacial reaction is 0.07%; The acyl chlorides monomer of two described degrees of functionality is terephthalyl chloride; Described three-functionality-degree acyl chlorides monomer is pyromellitic trimethylsilyl chloride.Described charged grafting functional layer is reacted by amino residual in active group molecule and crosslinked desalination layer and/or acyl chlorides and/or carboxylate radical to be prepared, and its surface charge density and kind are by the kind of active group molecule and regulating and controlling of quantities.
Its preparation method, comprises the following steps:
(1) prepare polysulfones casting solution after being mixed with pore former, solvent by polysulfones particle, and polysulfones casting solution is coated in nonwoven layer, and dipping is with water, obtains polysulfone porous supporting layer;
(2) fatty amines is mixed with into amine mixture with aromatic amine, acid binding agent and water, and the polysulfone porous supporting layer that step (1) obtains be impregnated in wherein, after the absorption of polysulfone porous supporting layer is saturated, take out, adopt nitrogen to remove the water droplet of remained on surface;
(3) after the acyl chlorides monomer of two degrees of functionality and the acyl chlorides monomer of three-functionality-degree being mixed into acyl chlorides monomer mixture, the polysulfone porous supporting layer that step (2) process terminates be impregnated in wherein, the crosslinked desalination layer of reaction preparation, after time to be impregnated reaches 15s, adopt nitrogen to remove the residual oil phase solvent of face under room temperature, the NF membrane of crosslinked desalination layer must be had;
(4) active group molecule is become after the aqueous solution with catalyst complex, again this aqueous solution be coated in the NF membrane surface with crosslinked desalination layer or the NF membrane with crosslinked desalination layer impregnated in the aqueous solution after 45s, be placed on 5min in baking oven again, obtain and the composite nanometer filtering film with high selectivity is removed to divalent ion.Temperature in baking oven in said method is 50 DEG C.Above-mentioned active group molecule is maleic anhydride.Above-mentioned active group molecule is after becoming the aqueous solution with catalyst complex, and wherein the mass concentration of active group molecule is 0.1%, and the mass concentration of catalyst is 0.01%.Above-mentioned catalyst is hydrochloric acid, and its mass concentration is 0.01%.Described acid binding agent is sodium carbonate, and mass concentration is 0.01%.Above-mentioned polysulfones particle and pore former, solvent, the mass ratio of its mixing is 15: 0.5: 74.Described pore former is polyvinyl alcohol.Described solvent is DMF.
Embodiment 2-embodiment 6
On the basis of embodiment 1, other changing contents on the basis of embodiment 1 are as follows:
Above-described embodiment is only limitted in actual production and operating process, make brief description to the present invention; the protection domain of technical scheme of the present invention can not be limited to absolutely; and in addition; this researcher is also by operating in laboratory, and the operation scheme concrete to it is presented as in following examples 7-10.
Embodiment 7
Configure 19% polysulfones solution, make porous polymer supporting layer through liquid-solid phase conversion method.Configuration containing the solution of 0.5wt% hexamethylene diamine and 2.0% m-phenylene diamine (MPD), and adds appropriate NaOH and pH value is adjusted to about 11, i.e. obtained mixed amine solution (solution A).Configuration 0.22wt% pyromellitic trimethylsilyl chloride solution (B solution), wherein solvent is cyclohexane.The glycerin ether aqueous solution (C solution) of configuration 0.3%, catalyst is hydrochloric acid, and concentration is 0.05%.Polysulfone porous supporting layer is soaked in solution A, dip time is 30s, after draining the face globule, enter B solution again, dip time is 20s, the cyclohexane of dry removing face at normal temperatures after taking-up, is placed in C solution by going out the diaphragm of cyclohexane, take out after 50s is put in leaching and heat-treat in the baking oven of 80 DEG C, processing time 5min.Diaphragm after process is taken out to be kept in pure water and detects.
Embodiment 8
Configure 19% polysulfones solution, make porous polymer supporting layer through liquid-solid phase conversion method.Configuration containing the solution of 0.1wt% hexamethylene diamine and 3.0% m-phenylene diamine (MPD), and adds appropriate NaOH and pH value is adjusted to about 11, i.e. obtained mixed amine solution (solution A).Configuration 0.22wt% pyromellitic trimethylsilyl chloride solution (B solution), wherein solvent is cyclohexane.The glycerin ether aqueous solution (C solution) of configuration 0.3%, catalyst is hydrochloric acid, and concentration is 0.05%.Polysulfone porous supporting layer is soaked in solution A, dip time is 30s, after draining the face globule, enter B solution again, dip time is 20s, the cyclohexane of dry removing face at normal temperatures after taking-up, is placed in C solution by going out the diaphragm of cyclohexane, take out after 50s is put in leaching and heat-treat in the baking oven of 80 DEG C, processing time 5min.Diaphragm after process is taken out to be kept in pure water and detects.
Embodiment 9
Configure 19% polysulfones solution, make porous polymer supporting layer through liquid-solid phase conversion method.Configuration containing the solution of 0.1wt% hexamethylene diamine and 3.0% m-phenylene diamine (MPD), and adds appropriate NaOH and pH value is adjusted to about 11, i.e. obtained mixed amine solution (solution A).Configuration 0.22wt% pyromellitic trimethylsilyl chloride solution (B solution), wherein solvent is cyclohexane.The glycerin ether aqueous solution (C solution) of configuration 1%, catalyst is hydrochloric acid, and concentration is 0.1%.Polysulfone porous supporting layer is soaked in solution A, dip time is 30s, after draining the face globule, enter B solution again, dip time is 20s, the cyclohexane of dry removing face at normal temperatures after taking-up, is placed in C solution by going out the diaphragm of cyclohexane, take out after 50s is put in leaching and heat-treat in the baking oven of 80 DEG C, processing time 5min.Diaphragm after process is taken out to be kept in pure water and detects.
Embodiment 10
Configure 19% polysulfones solution, make porous polymer supporting layer through liquid-solid phase conversion method.Configuration containing the solution of 0.5wt% hexamethylene diamine and 2.0% m-phenylene diamine (MPD), and adds appropriate NaOH and pH value is adjusted to about 11, i.e. obtained mixed amine solution (solution A).Configuration 0.22wt% pyromellitic trimethylsilyl chloride solution (B solution), wherein solvent is cyclohexane.The glycerin ether aqueous solution (C solution) of configuration 1%, catalyst is hydrochloric acid, and concentration is 0.1%.Polysulfone porous supporting layer is soaked in solution A, dip time is 30s, after draining the face globule, enter B solution again, dip time is 20s, the cyclohexane of dry removing face at normal temperatures after taking-up, is placed in C solution by going out the diaphragm of cyclohexane, take out after 50s is put in leaching and heat-treat in the baking oven of 50 DEG C, processing time 8min.Diaphragm after process is taken out to be kept in pure water and detects.

Claims (10)

1. one kind removes the composite nanometer filtering film with high selectivity to divalent ion, it is characterized in that, be made up of nonwoven layer, polysulfone porous supporting layer, the crosslinked desalination layer of mixing and charged grafting functional layer, wherein, polysulfone porous supporting layer is arranged in nonwoven layer, and crosslinked desalination layer and charged grafting functional layer are successively set on polysulfone porous supporting layer; Crosslinked desalination layer is prepared at profit phase interfacial reaction by amine mixture and acyl chlorides monomer mixture; Charged merit grafting ergosphere by surface physics or chemical graft in crosslinked desalination layer.
2. remove the composite nanometer filtering film with high selectivity to divalent ion as claimed in claim 1, it is characterized in that, described amine mixture is mixed by aliphatic amine and aromatic amine; Described acyl chlorides monomer mixture by the acyl chlorides monomer of the acyl chlorides monomer and three-functionality-degree with two degrees of functionality arbitrarily than mixing.
3. as claimed in claim 2 the composite nanometer filtering film with high selectivity is removed to divalent ion, it is characterized in that, described aliphatic amine is 1, 4-cyclohexanediamine, 1, 2-cyclohexanediamine, piperazine, ethylene glycol amine, ethylenediamine, propane diamine, butanediamine, hexamethylene diamine, monoethanolamine, polymine, triethylamine, three (2-aminoethyl) amine, diethylenetriamine, N-(2-ethoxy) ethylenediamine, 1, 3-cyclohexanediamine, 1, the two piperidyl propane of 3-, 4-aminomethylpiperazine, monoethanolamine, diethanol amine, hexylene glycol amine, at least one in diglycolamine.
4. as claimed in claim 2 the composite nanometer filtering film with high selectivity is removed to divalent ion, it is characterized in that, described aromatic amine is aniline, m-phenylene diamine (MPD), p-phenylenediamine (PPD), o-phenylenediamine, 1,3,5-tri-amido benzene, 1,2,4-tri-amido benzene, 3, at least one in 5-diaminobenzoic acid, 2,4-diaminotoluenes, 2,4-diamino anisoles, amidol, xylylene diamine.
5. remove the composite nanometer filtering film with high selectivity to divalent ion as claimed in claim 1, it is characterized in that, described amine mixture, its mass concentration when profit phase interfacial reaction is 1.5-5%.
6. as described in claim 1 or 2 or 5, remove the composite nanometer filtering film with high selectivity to divalent ion, it is characterized in that, described amine mixture, fatty amines accounts for the 0.5-50% of aromatic amine weight; More excellent is 1-10%.
7. remove the composite nanometer filtering film with high selectivity to divalent ion as claimed in claim 1 or 2, it is characterized in that, described acyl chlorides monomer mixture, its mass concentration when profit phase interfacial reaction is 0.07-0.4%; The acyl chlorides monomer of two described degrees of functionality is at least one in terephthalyl chloride, isophthaloyl chloride, phthalyl chlorine and biphenyl dimethyl chloride; Described three-functionality-degree acyl chlorides monomer is pyromellitic trimethylsilyl chloride.
8. as claimed in claim 1 the composite nanometer filtering film with high selectivity is removed to divalent ion, it is characterized in that, described charged grafting functional layer is reacted by amino residual in active group molecule and crosslinked desalination layer and/or acyl chlorides and/or carboxylate radical to be prepared, and its surface charge density and kind are by the kind of active group molecule and regulating and controlling of quantities.
9. remove the composite nanometer filtering film with high selectivity to divalent ion as claimed in claim 8, it is characterized in that, described active group molecule is at least containing a kind of molecule in carboxyl, acid anhydrides, epoxy radicals, acyl chlorides, sulfonic acid chloride, hydroxyl and amino.
10. preparation method divalent ion being removed to the composite nanometer filtering film with high selectivity as described in any one of claim 1-9, is characterized in that, comprise the following steps:
(1) prepare polysulfones casting solution after being mixed with pore former, solvent by polysulfones particle, and polysulfones casting solution is coated in nonwoven layer, and dipping is with water, obtains polysulfone porous supporting layer;
(2) fatty amines is mixed with into amine mixture with aromatic amine, acid binding agent and water, and the polysulfone porous supporting layer that step (1) obtains be impregnated in wherein, after the absorption of polysulfone porous supporting layer is saturated, take out, adopt nitrogen to remove the water droplet of remained on surface;
(3) after the acyl chlorides monomer of two degrees of functionality and the acyl chlorides monomer of three-functionality-degree being mixed into acyl chlorides monomer mixture, the polysulfone porous supporting layer that step (2) process terminates be impregnated in wherein, the crosslinked desalination layer of reaction preparation, after time to be impregnated reaches 15-25s, adopt nitrogen to remove the residual oil phase solvent of face under room temperature, the NF membrane of crosslinked desalination layer must be had;
(4) active group molecule is become after the aqueous solution with catalyst complex, again this aqueous solution be coated in the NF membrane surface with crosslinked desalination layer or the NF membrane with crosslinked desalination layer impregnated in the aqueous solution after 45-55s, be placed on 5-10min in baking oven again, obtain and the composite nanometer filtering film with high selectivity is removed to divalent ion.
CN201510952929.9A 2015-12-18 2015-12-18 A kind of composite nanometer filtering film to divalent ion removing with high selectivity and preparation method thereof Active CN105435653B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510952929.9A CN105435653B (en) 2015-12-18 2015-12-18 A kind of composite nanometer filtering film to divalent ion removing with high selectivity and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510952929.9A CN105435653B (en) 2015-12-18 2015-12-18 A kind of composite nanometer filtering film to divalent ion removing with high selectivity and preparation method thereof

Publications (2)

Publication Number Publication Date
CN105435653A true CN105435653A (en) 2016-03-30
CN105435653B CN105435653B (en) 2018-02-06

Family

ID=55546549

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510952929.9A Active CN105435653B (en) 2015-12-18 2015-12-18 A kind of composite nanometer filtering film to divalent ion removing with high selectivity and preparation method thereof

Country Status (1)

Country Link
CN (1) CN105435653B (en)

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106582315A (en) * 2016-11-29 2017-04-26 华中科技大学 Polyamide composite membrane and preparation method thereof
CN106914152A (en) * 2017-03-28 2017-07-04 华中科技大学 A kind of polyamide film composite membrane and its preparation method and application
CN109200823A (en) * 2018-08-28 2019-01-15 浙江工业大学 A kind of preparation method and application for the ecosystem positively charged nanofiltration membranes that polyethyleneimine is amine-modified
CN110947307A (en) * 2019-11-28 2020-04-03 烟台金正环保科技有限公司 Preparation method of composite desalination layer nanofiltration membrane
CN112619420A (en) * 2019-09-24 2021-04-09 天津天元新材料科技有限公司 Loofah sponge modified composite reverse osmosis membrane and preparation method thereof
CN113385047A (en) * 2021-05-10 2021-09-14 清华大学 Separation membrane for water treatment and preparation method and application thereof
CN113398781A (en) * 2021-06-18 2021-09-17 中国农业科学院农业质量标准与检测技术研究所 Microporous filter membrane material and preparation method and application thereof
CN113457449A (en) * 2021-07-26 2021-10-01 中国海洋大学 Polyamide nanofiltration membrane with multivalent/monovalent salt selectivity and preparation method thereof
CN113750798A (en) * 2020-06-01 2021-12-07 天津工业大学 Preparation method of double electric layer composite nanofiltration membrane
CN114191992A (en) * 2021-12-22 2022-03-18 湖南澳维环保科技有限公司 Composite nanofiltration membrane for extracting lithium from salt lake and preparation method thereof
CN114471183A (en) * 2020-11-11 2022-05-13 沃顿科技股份有限公司 Method for producing separation membrane and separation membrane produced thereby
CN114713295A (en) * 2022-04-22 2022-07-08 河北工业大学 Monovalent selective cation exchange membrane and preparation method and application thereof
CN114870629A (en) * 2022-06-06 2022-08-09 天津工业大学 High-selectivity nanofiltration membrane and preparation method and application thereof
CN115253697A (en) * 2021-04-29 2022-11-01 天津膜天膜科技股份有限公司 Preparation method of nanofiltration membrane for efficiently removing hardness
CN115364669A (en) * 2022-08-19 2022-11-22 东华理工大学 Charged Janus nanofiltration membrane and preparation method thereof
CN115991560A (en) * 2023-03-22 2023-04-21 深圳永清水务有限责任公司 Treatment method for recycling iron phosphate production wastewater

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1935678A (en) * 2006-09-20 2007-03-28 江南大学 Clean production method for treating electroplating waste water by nano filtering process
CN101462024A (en) * 2008-12-24 2009-06-24 北京时代沃顿科技有限公司 Composite reverse osmosis membrane with high-intensity anti-pollution layer and preparation method thereof
CN101462025A (en) * 2008-08-13 2009-06-24 贵阳时代汇通膜科技有限公司 Double-layer polyamide surface layer composite reverse osmosis membrane and preparation method thereof
CN101934201A (en) * 2009-06-29 2011-01-05 北京时代沃顿科技有限公司 High-selectivity composite nanofiltration membrane and preparation method thereof
CN201832563U (en) * 2010-10-08 2011-05-18 北京能泰高科环保技术有限公司 Vanadium and sodium separating device
CN102139187A (en) * 2010-01-28 2011-08-03 中国科学院化学研究所 Hyperfiltration membrane or nanofiltration membrane with multi-layered composite structure and preparation method thereof
CN102921318A (en) * 2012-11-21 2013-02-13 海南立昇净水科技实业有限公司 External-pressure type charged hollow fiber nano-filtration membrane and preparation method therefor
CN103480286A (en) * 2013-07-26 2014-01-01 北京碧水源膜科技有限公司 Preparation method for UV-induced photografted charged nanofiltration membrane and product thereof, and application of product
US20140338429A1 (en) * 2011-06-03 2014-11-20 Waters Technologies Corporation Method of separation of lipid and biological molecular species using high purity chromatographic materials comprising an ionizable modifier
CN104941461A (en) * 2014-03-27 2015-09-30 贵阳时代沃顿科技有限公司 Nanofiltration membrane for seawater desalination and preparation method thereof

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1935678A (en) * 2006-09-20 2007-03-28 江南大学 Clean production method for treating electroplating waste water by nano filtering process
CN101462025A (en) * 2008-08-13 2009-06-24 贵阳时代汇通膜科技有限公司 Double-layer polyamide surface layer composite reverse osmosis membrane and preparation method thereof
CN101462024A (en) * 2008-12-24 2009-06-24 北京时代沃顿科技有限公司 Composite reverse osmosis membrane with high-intensity anti-pollution layer and preparation method thereof
CN101934201A (en) * 2009-06-29 2011-01-05 北京时代沃顿科技有限公司 High-selectivity composite nanofiltration membrane and preparation method thereof
CN102139187A (en) * 2010-01-28 2011-08-03 中国科学院化学研究所 Hyperfiltration membrane or nanofiltration membrane with multi-layered composite structure and preparation method thereof
CN201832563U (en) * 2010-10-08 2011-05-18 北京能泰高科环保技术有限公司 Vanadium and sodium separating device
US20140338429A1 (en) * 2011-06-03 2014-11-20 Waters Technologies Corporation Method of separation of lipid and biological molecular species using high purity chromatographic materials comprising an ionizable modifier
CN102921318A (en) * 2012-11-21 2013-02-13 海南立昇净水科技实业有限公司 External-pressure type charged hollow fiber nano-filtration membrane and preparation method therefor
CN103480286A (en) * 2013-07-26 2014-01-01 北京碧水源膜科技有限公司 Preparation method for UV-induced photografted charged nanofiltration membrane and product thereof, and application of product
CN104941461A (en) * 2014-03-27 2015-09-30 贵阳时代沃顿科技有限公司 Nanofiltration membrane for seawater desalination and preparation method thereof

Cited By (23)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106582315A (en) * 2016-11-29 2017-04-26 华中科技大学 Polyamide composite membrane and preparation method thereof
CN106914152A (en) * 2017-03-28 2017-07-04 华中科技大学 A kind of polyamide film composite membrane and its preparation method and application
CN109200823A (en) * 2018-08-28 2019-01-15 浙江工业大学 A kind of preparation method and application for the ecosystem positively charged nanofiltration membranes that polyethyleneimine is amine-modified
CN112619420A (en) * 2019-09-24 2021-04-09 天津天元新材料科技有限公司 Loofah sponge modified composite reverse osmosis membrane and preparation method thereof
CN110947307A (en) * 2019-11-28 2020-04-03 烟台金正环保科技有限公司 Preparation method of composite desalination layer nanofiltration membrane
CN110947307B (en) * 2019-11-28 2020-08-28 烟台金正环保科技有限公司 Preparation method of composite desalination layer nanofiltration membrane
CN113750798A (en) * 2020-06-01 2021-12-07 天津工业大学 Preparation method of double electric layer composite nanofiltration membrane
CN113750798B (en) * 2020-06-01 2022-07-19 天津工业大学 Preparation method of double electric layer composite nanofiltration membrane
CN114471183A (en) * 2020-11-11 2022-05-13 沃顿科技股份有限公司 Method for producing separation membrane and separation membrane produced thereby
CN114471183B (en) * 2020-11-11 2023-03-14 沃顿科技股份有限公司 Method for producing separation membrane and separation membrane produced thereby
CN115253697A (en) * 2021-04-29 2022-11-01 天津膜天膜科技股份有限公司 Preparation method of nanofiltration membrane for efficiently removing hardness
CN115253697B (en) * 2021-04-29 2023-12-26 天津膜天膜科技股份有限公司 Preparation method of nanofiltration membrane capable of efficiently removing hardness
CN113385047A (en) * 2021-05-10 2021-09-14 清华大学 Separation membrane for water treatment and preparation method and application thereof
CN113398781A (en) * 2021-06-18 2021-09-17 中国农业科学院农业质量标准与检测技术研究所 Microporous filter membrane material and preparation method and application thereof
CN113457449A (en) * 2021-07-26 2021-10-01 中国海洋大学 Polyamide nanofiltration membrane with multivalent/monovalent salt selectivity and preparation method thereof
CN113457449B (en) * 2021-07-26 2022-05-24 中国海洋大学 Polyamide nanofiltration membrane with multivalent/monovalent salt selectivity and preparation method thereof
CN114191992A (en) * 2021-12-22 2022-03-18 湖南澳维环保科技有限公司 Composite nanofiltration membrane for extracting lithium from salt lake and preparation method thereof
CN114191992B (en) * 2021-12-22 2023-11-10 湖南澳维科技股份有限公司 Composite nanofiltration membrane for extracting lithium from salt lake and preparation method thereof
CN114713295A (en) * 2022-04-22 2022-07-08 河北工业大学 Monovalent selective cation exchange membrane and preparation method and application thereof
CN114870629A (en) * 2022-06-06 2022-08-09 天津工业大学 High-selectivity nanofiltration membrane and preparation method and application thereof
CN114870629B (en) * 2022-06-06 2023-06-30 天津工业大学 High-selectivity nanofiltration membrane and preparation method and application thereof
CN115364669A (en) * 2022-08-19 2022-11-22 东华理工大学 Charged Janus nanofiltration membrane and preparation method thereof
CN115991560A (en) * 2023-03-22 2023-04-21 深圳永清水务有限责任公司 Treatment method for recycling iron phosphate production wastewater

Also Published As

Publication number Publication date
CN105435653B (en) 2018-02-06

Similar Documents

Publication Publication Date Title
CN105435653A (en) Composite nano filtration membrane with high selectivity on removing divalent ions and preparation method thereof
Zheng et al. Facile fabrication of a positively charged nanofiltration membrane for heavy metal and dye removal
Lee et al. Performance, limitation, and opportunities of acid-resistant nanofiltration membranes for industrial wastewater treatment
Thong et al. Molecular design of nanofiltration membranes for the recovery of phosphorus from sewage sludge
WO2016002821A1 (en) Composite semipermeable membrane
CN106582299B (en) A kind of graphene-based 3D modified by nano particles organic separation membrane preparation method of ammoxidation
Huang et al. Enhancing nanofiltration performance for antibiotics/NaCl separation via water activation before microwave heating
EP2883600A2 (en) Polyamide-based water-treatment separation membrane having excellent salt removal rate and permeation flux characteristics and method for manufacturing same
JP6197969B1 (en) Composite semipermeable membrane
KR20170021798A (en) Composite semipermeable membrane
WO2018063122A2 (en) Forward osmosis membrane obtained by using sulfonated polysulfone (spsf) polymer and production method thereof
CN113083032A (en) Positively charged blended ultrafiltration membrane and preparation method thereof
Yang et al. Fabrication of hollow fiber loose nanofiltration separation layers based on nucleophilic addition and Schiff base reactions and the investigation on separation performance of low molecular weight dye/salt systems
CN111346526B (en) Hollow fiber nanofiltration membrane and preparation method thereof
CN113842783B (en) Acid-resistant high-flux polyarylether composite nanofiltration membrane, and preparation method and application thereof
CN205340595U (en) A compound laminar industry membrane for water treatment
JP5018306B2 (en) Method for improving rejection rate of permeable membrane, permeable membrane processing method and apparatus
CN108430612B (en) Composite semipermeable membrane
JP2009262089A (en) Manufacturing method of composite semi-permeable membrane
CN114471197A (en) Mixed charged nanofiltration membrane as well as preparation method and application thereof
JP2021069989A (en) Composite semipermeable membrane
CN115178102A (en) Alkali stable semipermeable membranes and methods therefor
Li et al. Preparation of dense polysulfonamide acid-resistant composite membrane with high rejection based on polyethylene substrate
CN103055723A (en) Cross-linking type polybenzimidazole porous separation membrane and preparation method and application thereof
Chendake et al. Transport of inorganic acids through polybenzimidazole (PBI) based membranes by chemo-dialysis

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CP03 Change of name, title or address

Address after: 550000 1518 Li Yang Avenue, Guiyang national hi tech Industrial Development Zone, Guiyang, Guizhou

Patentee after: Time Walton Technology Co., Ltd.

Address before: 550018 206, 2 / F, office building, South Guizhou science and Technology Industrial Park, Guiyang hi tech Zone.

Patentee before: Vontron Technology Co., Ltd.

CP03 Change of name, title or address
TR01 Transfer of patent right

Effective date of registration: 20211116

Address after: 550000 No. 1518, Liyang Avenue, Guiyang National High tech Industrial Development Zone, Guiyang City, Guizhou Province

Patentee after: Wharton Technology Co., Ltd

Address before: 550000 No. 1518, Liyang Avenue, Guiyang National High tech Industrial Development Zone, Guiyang City, Guizhou Province

Patentee before: Time Wharton Technology Co., Ltd

TR01 Transfer of patent right