阅读说明：本技术 一种耐氯抗污染软水用纳滤膜及其制备方法 (Nanofiltration membrane for chlorine-resistant and pollution-resistant soft water and preparation method thereof ) 是由 孔新 范琳 阚红强 赵永锋 全晓 赵伟国 孙家宽 于 2020-04-30 设计创作，主要内容包括：本发明提供一种耐氯抗污染软水用纳滤膜及其制备方法,所述纳滤膜包括聚砜基膜,所述聚砜基膜上依次覆盖聚哌嗪酰胺层和表面改性层；其中,所述表面改性层是由二氧化硫脲和聚乙烯醇在聚哌嗪酰胺层表面反应而成。该纳滤膜具有传统分盐纳滤膜的优势,同时具备优异的硬度脱除能力以及耐氯和抗污染性能,改性后的纳滤膜耐氯以及抗污染性能得到显著提升,能够维持其较高的氯化钙截留率。本发明制备的纳滤膜在水源地水质较硬或以地下水为水源的市政饮用水深度处理领域具有广阔的应用前景。(The invention provides a nanofiltration membrane for chlorine-resistant and pollution-resistant soft water and a preparation method thereof, wherein the nanofiltration membrane comprises a polysulfone base membrane, and a polypiperazine amide layer and a surface modification layer are sequentially covered on the polysulfone base membrane; the surface modification layer is formed by reacting thiourea dioxide and polyvinyl alcohol on the surface of the polypiperazine amide layer. The nanofiltration membrane has the advantages of the traditional salt separation nanofiltration membrane, and has excellent hardness removal capacity, chlorine resistance and pollution resistance, the chlorine resistance and pollution resistance of the modified nanofiltration membrane are remarkably improved, and the high calcium chloride rejection rate of the nanofiltration membrane can be maintained. The nanofiltration membrane prepared by the invention has wide application prospect in the field of advanced treatment of municipal drinking water with hard water quality in water source places or with underground water as a water source.)

1. A nanofiltration membrane for chlorine-resistant and pollution-resistant soft water is characterized by comprising a polysulfone base membrane, wherein a polypiperazine amide layer and a surface modification layer are sequentially covered on the polysulfone base membrane;

the surface modification layer is formed by reacting thiourea dioxide and polyvinyl alcohol on the surface of the polypiperazine amide layer.

2. The nanofiltration membrane of claim 1, wherein the polysulfone-based membrane is prepared by dissolving polysulfone and copovidone in N, N-dimethylformamide and performing immersion phase conversion; and/or

The polypiperazine amide layer is prepared by immersing a polysulfone base membrane impregnated with piperazine and an acid absorbent into a trimesoyl chloride oil phase solution for interfacial polymerization reaction.

3. A method for preparing a nanofiltration membrane for chlorine-resistant and pollution-resistant soft water according to claim 1 or 2, which comprises the following steps:

(1) dissolving polysulfone and copovidone in N, N-dimethylformamide to prepare a membrane casting solution, then coating the membrane casting solution on polyester non-woven fabric, immersing the polyester non-woven fabric in water to form a membrane through phase inversion, and taking out the membrane to obtain a polysulfone base membrane;

(2) soaking the polysulfone basal membrane prepared in the step (1) by adopting a mixed aqueous solution of piperazine and an acid absorbent, separating and removing membrane surface liquid, soaking the polysulfone basal membrane into trimesoyl chloride oil phase solution for interfacial polymerization reaction, and separating and removing the membrane surface liquid to obtain a polysulfone basal membrane covering a polypiperazine amide layer;

(3) and (3) immersing the polysulfone base membrane covered with the polypiperazine amide layer obtained in the step (2) into a mixed aqueous solution of thiourea oxide and polyvinyl alcohol for reaction, and then separating, drying and washing to obtain the chlorine-resistant and pollution-resistant nanofiltration membrane for soft water.

4. The preparation method according to claim 3, wherein the membrane casting solution in the step (1) has a polysulfone concentration of 15-22 wt%, preferably 18-20 wt%; the concentration of the copovidone is 0.1-5.0 wt%, preferably 0.5-1.5 wt%;

preferably, the copovidone is selected from one or more of VA28, VA55, VA64 and VA73, and is preferably VA 64.

5. The preparation method according to claim 3 or 4, wherein the thickness of the casting solution scraped and coated on the polyester non-woven fabric in the step (1) is 50-500 μm, preferably 100-200 μm; and/or

The phase transformation in the step (1) is carried out to form a film, wherein the temperature is 10-60 ℃, and preferably 25-40 ℃; the time is 10 to 120s, preferably 20 to 60 s.

6. The production method according to any one of claims 3 to 5, wherein the mixed aqueous solution of piperazine and an acid scavenger in the step (2) has a concentration of 0.2 to 4.0 wt%, preferably 1.0 to 2.0 wt%; the concentration of the acid acceptor is 1.0-3.0 wt%, preferably 2.0-2.5 wt%;

preferably, the acid scavenger is selected from one or more of trisodium phosphate, sodium hydroxide, sodium carbonate and triethylamine, more preferably trisodium phosphate.

7. The method according to any one of claims 3 to 6, wherein the trimesoyl chloride oil phase solution in step (2) comprises trimesoyl chloride and an organic solvent, wherein the concentration of the trimesoyl chloride is 0.05 to 0.5 wt%, preferably 0.1 to 0.2 wt%;

preferably, the organic solvent is selected from one or more of n-hexane, cyclohexane, ethylcyclohexane, n-heptane and isoparaffin solvents, more preferably an isoparaffin solvent having a boiling point above 160 ℃, selected from one or more of Isopar G, Isopar H and Isopar L.

8. The method according to any one of claims 3 to 7, wherein the dipping treatment in the step (2) is carried out for 1 to 5min, preferably 1 to 3 min; and/or

The interfacial polymerization reaction is carried out for 20-90 s, preferably 40-60 s.

9. The method according to any one of claims 3 to 8, wherein the mixed aqueous solution of thiourea dioxide and polyvinyl alcohol in step (3) has a thiourea dioxide concentration of 0.1 to 1.0 wt%, preferably 0.2 to 0.6 wt%, and the polyvinyl alcohol concentration of 0.2 to 2.0 wt%, preferably 0.4 to 1.0 wt%.

10. The method according to any one of claims 3 to 8, wherein the reaction temperature in the step (3) is 20 to 60 ℃, preferably 25 to 40 ℃; the reaction time is 10-30 s, preferably 15-20 s; and/or

Drying at the temperature of 60-110 ℃, preferably 70-90 ℃; the time is 5-10 min, preferably 6-8 min.

Technical Field

The invention belongs to the technical field of water treatment membranes, and particularly relates to a nanofiltration membrane for chlorine-resistant and pollution-resistant soft water and a preparation method thereof.

Background

Nanofiltration is a pressure-driven membrane separation process between reverse osmosis and ultrafiltration, and the core of the nanofiltration technology is a nanofiltration membrane. The largest application field of the nanofiltration membrane is the softening of drinking water and the removal of organic matters. The nanofiltration membrane can intercept microorganisms, bacteria and pathogens in water, and can effectively reduce the water hardness, and effectively remove chromaticity, heavy metals and small-molecule organic pollutants (natural organic matters, disinfection byproducts, pesticides, endocrine disruptors, personal protective articles, medicines and the like), thereby greatly improving the safety of drinking water. Therefore, people pay more attention to the 'drinking water advanced treatment technology' taking the nanofiltration membrane as a core.

Interfacial polymerization is currently the most widely used method for preparing composite nanofiltration/reverse osmosis membranes. The method mainly comprises the step of performing polycondensation reaction on a water phase monomer containing polyamino and an oil phase monomer containing polyacyl chloride at a two-phase interface, so that a polyamide functional layer with selective permeability is formed on the surface of a supporting base film, and the separation performance of the composite film is determined. The two aqueous phase monomers most commonly used in the preparation of commercial composite nanofiltration membranes at present are meta-phenylenediamine (MPD) and piperazine (PIP), respectively. Research shows that MPD and PIP have obvious difference in separating performance of corresponding nanofiltration membrane prepared through reaction with polyacyl chloride due to different molecular structures. MPD is generally used as an aqueous phase reaction monomer in the preparation process of the reverse osmosis membrane, the nanofiltration membrane prepared based on the MPD monomer has high overall desalination rate and is generally called as a desalination nanofiltration membrane, and the nanofiltration membrane prepared by reacting PIP with trimesoyl chloride (TMC) has high monovalent/divalent ion selectivity and is generally called as a salt separation nanofiltration membrane. Due to the difference of the reaction monomer properties, the two types of nanofiltration membranes have difference in the selection of the application.

The desalination nanofiltration membrane has high rejection rate on calcium ions and magnesium ions, is mainly used in the field of drinking water softening, can effectively reduce water hardness, but has high rejection rate on sodium chloride, such as NF90 of DuPont and TMN20H of Dongli, the rejection rate on sodium chloride is more than 90%, and the membrane element has low water yield, so that the problems of low pH value of produced water, damage to a water supply network, low system recovery rate, high operation energy consumption and the like can be caused in municipal drinking water treatment. The salt separating nanofiltration membrane has the advantages of large water yield, high system recovery rate, low operation energy consumption and the like because of low rejection rate to sodium chloride and low osmotic pressure on two sides of a required membrane, and simultaneously the pH value of produced water is more than 7.0, so that the influence on a city water supply network can not be caused, but the rejection rate of calcium ions of the existing commercialized salt separating nanofiltration membrane, such as NF270 of DuPont company, is low (40-60%), and the water hardness can not be effectively reduced, and the purified water taste can not be improved.

Aiming at the defect of poor hardness removal capability of the salt-splitting nanofiltration membrane, most researchers prepare a polyamide layer with positive surface charge by adopting reaction monomers or polymers with higher cation density, such as polyethylene polyamine, polyethylene imine or chitosan, for interfacial polymerization, and improve the rejection rate of divalent cations by utilizing the charge repulsion effect. However, nanofiltration membranes prepared by modifying the surface charge properties of polyamide layers encounter many problems in practical use. For example, since most of the surfaces of colloidal particles present in natural water bodies are generally negatively charged, the positively charged nanofiltration membrane surface causes serious pollution problems due to adsorption of the colloidal particles. In addition, because the municipal tap water is generally added with the disinfectant such as sodium hypochlorite, chlorine dioxide and the like, the raw water often contains residual active chlorine with certain concentration, and rich amino groups on the surface of the positively charged nanofiltration membrane are easily destroyed by the oxidation of the active chlorine, so that the charge rejection effect is weakened, and the desalination rate of the nanofiltration membrane is reduced.

In addition, researchers regulate and control the polyamide cross-linking structure by adopting a method of mixing and cross-linking aromatic amine and aliphatic amine, and although the rejection rate of the nanofiltration membrane on divalent cations can be improved by using the method, the water flux of the prepared nanofiltration membrane is generally low, the surface roughness of the membrane is large, and the anti-pollution performance of the membrane is reduced.

Disclosure of Invention

The invention aims to provide a chlorine-resistant and pollution-resistant nanofiltration membrane for soft water, aiming at the problems of the nanofiltration membrane, wherein the nanofiltration membrane has the advantages of the traditional salt separation nanofiltration membrane, and simultaneously has excellent hardness removal capability, chlorine resistance and pollution resistance.

The invention also aims to provide a preparation method of the nanofiltration membrane.

In order to achieve the purpose, the invention adopts the following technical scheme:

a nanofiltration membrane for chlorine-resistant and pollution-resistant soft water comprises a polysulfone base membrane, wherein a polypiperazine amide layer and a surface modification layer are sequentially covered on the polysulfone base membrane;

the surface modification layer is formed by reacting thiourea dioxide and polyvinyl alcohol on the surface of the polypiperazine amide layer.

Further, the polysulfone-based membrane is prepared by dissolving polysulfone and copovidone in N, N-dimethylformamide through an immersion phase inversion method.

Further, the polypiperazine amide layer is prepared by immersing a polysulfone base membrane with piperazine and an acid absorbent impregnated on the surface into a trimesoyl chloride oil phase solution for interfacial polymerization.

A preparation method of a nanofiltration membrane for chlorine-resistant and pollution-resistant soft water comprises the following steps:

(1) preparation of polysulfone-based membrane: dissolving polysulfone and copovidone in N, N-dimethylformamide to prepare a membrane casting solution, then coating the membrane casting solution on polyester non-woven fabric, immersing the polyester non-woven fabric in water to form a membrane through phase inversion, and taking out the membrane to obtain a polysulfone base membrane;

(2) preparation of polypiperazine amide layer: soaking the polysulfone basal membrane prepared in the step (1) by adopting a mixed aqueous solution of piperazine and an acid absorbent, separating and removing membrane surface liquid, soaking the polysulfone basal membrane into trimesoyl chloride oil phase solution for interfacial polymerization reaction, and separating and removing the membrane surface liquid to obtain a polysulfone basal membrane covering a polypiperazine amide layer;

(3) preparation of the surface modification layer: and (3) immersing the polysulfone base membrane covered with the polypiperazine amide layer obtained in the step (2) into a mixed aqueous solution of thiourea oxide and polyvinyl alcohol for reaction, and then separating, drying and washing to obtain the chlorine-resistant and pollution-resistant nanofiltration membrane for soft water.

Preferably, in the membrane casting solution in the step (1), the concentration of polysulfone is 15-22 wt%, preferably 18-20 wt%; the concentration of the copovidone is 0.1-5.0 wt%, preferably 0.5-1.5 wt%;

further preferably, the copovidone is selected from one or more of VA28, VA55, VA64 and VA73, preferably VA 64.

Preferably, the thickness of the casting solution coated on the polyester non-woven fabric in the step (1) is 50 to 500 μm, and preferably 100 to 200 μm.

Preferably, the phase transformation in the step (1) is carried out to form a film, and the temperature is 10-60 ℃, preferably 25-40 ℃; the time is 10 to 120s, preferably 20 to 60 s.

In some specific examples of the present invention, the step (1) employs the following operations: dissolving polysulfone and copovidone VA64 in N, N-dimethylformamide to prepare a casting solution with the polysulfone concentration of 15-22 wt% and the copovidone concentration of 0.1-5.0 wt%, then coating the casting solution on a polyester non-woven fabric, immersing the polyester non-woven fabric in water at 10-60 ℃ for 10-120 s to form a film by phase inversion, and taking out the film to obtain the polysulfone base film.

Preferably, the mixed aqueous solution of piperazine and an acid acceptor in the step (2), wherein the concentration of piperazine is 0.2-4.0 wt%, preferably 1.0-2.0 wt%; the concentration of the acid acceptor is 1.0-3.0 wt%, preferably 2.0-2.5 wt%;

further preferably, the acid scavenger is selected from one or more of trisodium phosphate, sodium hydroxide, sodium carbonate and triethylamine, more preferably trisodium phosphate.

Preferably, the immersion treatment in the step (2) is performed for 1 to 5min, preferably 1 to 3 min. The impregnation treatment is a conventional operation, the dosage of the impregnation liquid is not specifically required, and the base film can be completely impregnated.

Preferably, the trimesoyl chloride oil-phase solution in the step (2) comprises trimesoyl chloride and an organic solvent, wherein the concentration of the trimesoyl chloride is 0.05-0.5 wt%, preferably 0.1-0.2 wt%;

further preferably, the organic solvent is selected from one or more of n-hexane, cyclohexane, ethylcyclohexane, n-heptane and isoalkane solvents, more preferably isoalkane solvents having a boiling point higher than 160 ℃, and the isoalkane solvents having a boiling point higher than 160 ℃ are selected from mixed solvents of one or more of Isopar G, Isopar H and Isopar L.

Preferably, the interfacial polymerization reaction in the step (2) is performed at room temperature, and the reaction time is 20 to 90 seconds, preferably 40 to 60 seconds. In the step (2), when the basement membrane is immersed in the trimesoyl chloride oil phase solution for interfacial polymerization reaction, no specific requirement is imposed on the dosage of the oil phase solution, and the basement membrane can be completely immersed.

In some specific examples of the present invention, the step (2) employs the following operations: fixing the polysulfone base membrane obtained in the step (1), pouring a prepared mixed aqueous solution of piperazine and an acid-absorbing agent on the surface of the polysulfone base membrane, soaking for 1-5 min, pouring the solution, removing residual liquid on the surface of the base membrane, then pouring a prepared trimesoyl chloride oil phase solution on the surface of the membrane, completely soaking the base membrane into the oil phase solution, carrying out interfacial polymerization reaction at room temperature for 20-90 s, pouring the solution after the reaction is finished, and uniformly blowing by using an air knife or an air knife until no residual liquid exists on the surface of the membrane, thus obtaining the polysulfone base membrane covering the polypiperazine amide layer.

Preferably, the mixed aqueous solution of thiourea dioxide and polyvinyl alcohol in the step (3) has a thiourea dioxide concentration of 0.1 to 1.0 wt%, preferably 0.2 to 0.6 wt%, and the polyvinyl alcohol concentration of 0.2 to 2.0 wt%, preferably 0.4 to 1.0 wt%.

Preferably, the reaction temperature in the step (3) is 20-60 ℃, preferably 25-40 ℃; the reaction time is 10-30 s, preferably 15-20 s. In the step (3), when the base membrane is immersed into the mixed aqueous solution of thiourea oxide and polyvinyl alcohol for reaction, no specific requirement is imposed on the dosage of the mixed aqueous solution, and the polysulfone base membrane covered with the polypiperazine amide layer can be completely immersed.

Preferably, the drying in the step (3) is carried out at the temperature of 60-110 ℃, and preferably 70-90 ℃; the time is 5-10 min, preferably 6-8 min. The drying operation is preferably carried out by heating in an oven.

In some specific examples of the present invention, the step (3) adopts the following operations: pouring the prepared mixed solution of thiourea dioxide and polyvinyl alcohol onto the surface of the polysulfone base membrane covered with the polypiperazine amide layer formed in the step (2) for chemical reaction at the temperature of 20-60 ℃ for 10-30 s, pouring the solution after the reaction is finished, putting the membrane into a 60-110 ℃ drying oven for heat treatment for 5-10 min, and finally taking out the membrane and washing with water to obtain the chlorine-resistant and pollution-resistant nanofiltration membrane for soft water.

The application of the nanofiltration membrane for the chlorine-resistant and pollution-resistant soft water can be used in the field of water treatment, and is preferably used in the field of advanced treatment of municipal drinking water with harder water quality or using underground water as a water source.

Generally, the key of the preparation of the nanofiltration membrane by using the interfacial polymerization method is the selection of a supporting base membrane and the control of the distribution coefficient and the diffusion speed of a reaction monomer in two phases so as to rationalize the loosening degree of a polyamide layer on the surface of the base membrane. Because the dispersion of the reaction monomer PIP on the surface of the hydrophobic polysulfone base membrane is poor, in the preparation process of the supporting base membrane, additives such as N-vinyl-2-pyrrolidone (PVP), polyethylene glycol (PEG) and the like are usually added to improve the hydrophilicity of the surface of the polysulfone base membrane, but the additives are easy to run off in the phase inversion membrane forming process and are extremely non-uniform in distribution on the surface of the base membrane, so that the effect of dispersing the water phase reaction monomer on the surface of the base membrane is limited.

The copovidone adopted by the invention is a water-soluble copolymer synthesized by PVP and vinyl acetate according to a specific ratio (particularly, the ratio of VA64 is about 60:40), and compared with other PVP, the copovidone has the advantage that the water absorption rate is reduced because the molecules contain hydrophobic vinyl acetate groups. The method is characterized in that copovidone such as VA64 is added into a membrane casting solution to prepare the hydrophilic polysulfone base membrane, on one hand, a better winding effect is formed between a hydrophobic group in a high molecular chain segment and a polysulfone high molecular chain, so that more VA64 can be kept in holes of the polysulfone base membrane, on the other hand, VA64 uniformly spread in the holes of the base membrane plays a role of a surfactant, polar lactam groups in molecules effectively improve the dispersibility of PIP monomers on the surface of the base membrane, and the method is favorable for the PIP monomers to react with TMC in an interfacial polymerization process to form a high molecular chain interpenetrating network structure with higher crosslinking degree and regularity, and the generated polyamide network has small aperture and uniform hole distribution, so that the rejection rate of the nanofiltration membrane on calcium ions is remarkably improved.

In addition, in order to avoid chlorination of amide bonds (the chlorination of the amide bonds can destroy hydrogen bonds among polyamide molecules, so that the regularity of a polymer chain is reduced, the polymer chain is changed from a crystalline state to an amorphous state, a part of reticular pore structures in the polyamide are deformed, the calcium ion retention rate is reduced, and the chlorine resistance and the pollution resistance of the nanofiltration membrane are improved, thiourea dioxide and polyvinyl alcohol are introduced to chemically modify the surface of the generated polypiperazine amide layer. Thiourea dioxide is an inorganic compound, has strong reducibility, and has the characteristics of high reduction potential, slow reduction potential drop speed and the like; the polyvinyl alcohol is usually used for preparing a physical protective layer on the surface of the membrane, and can be quickly washed away in the use process due to no chemical bond action with the surface of the membrane (in the prior art, crosslinking agents such as glutaraldehyde are adopted for crosslinking under the heating condition, and can be retained on the surface of the membrane, so that the nanofiltration membrane is endowed with better anti-pollution performance, but more water flux can be sacrificed), and the chlorine resistance and the anti-pollution performance of the nanofiltration membrane can be improved and the loss of the polyvinyl alcohol in the use process can be reduced by using thiourea dioxide and the polyvinyl alcohol in a compounding manner.

The thiourea dioxide molecule contains hydroxyl groups and has strong hydrogen bond effect with polyvinyl alcohol, the mixed solution of the hydroxyl groups and the polyvinyl alcohol is poured on the surface of the polypiperazine amide layer for chemical reaction, the thiourea dioxide is grafted on the surface of the membrane through reaction with the residual acyl chloride groups in the polyamide layer, the polyvinyl alcohol having strong hydrogen bond effect with the thiourea dioxide is introduced into the polyamide layer at the same time, a small amount of polyvinyl alcohol uniformly spread on the surface of the membrane can not influence the water flux of the membrane, and can stably exist on the surface of the membrane. The modification effect of the mixture of thiourea dioxide and polyvinyl alcohol on the prepared nanofiltration membrane is shown in the following that, on one hand, when the membrane is contacted with an active chlorine solution, the thiourea dioxide on the surface of the membrane and the active chlorine have higher reaction activity, so that the hydrogen bonds between the molecules of the polypiperazine amide are protected from being damaged, and on the other hand, the hydroxyl group of the polyvinyl alcohol can effectively level the surface of the membrane, reduce the adhesion of pollutants, and further improve the anti-pollution performance of the nanofiltration membrane.

Compared with the prior art, the invention has the beneficial effects that:

the surface of the formed polypiperazine amide layer is modified by using the mixture of thiourea dioxide and polyvinyl alcohol, so that the chlorine resistance and pollution resistance of the modified nanofiltration membrane are remarkably improved, and the higher calcium chloride rejection rate of the nanofiltration membrane can be maintained. The nanofiltration membrane prepared by the invention has wide application prospect in the field of advanced treatment of municipal drinking water with hard water quality in water source places or with underground water as a water source.

According to the invention, the interface polymerization is carried out on the polysulfone base membrane containing the copovidone VA64 to form the polypiperazine amide structure with higher crosslinking degree and regularity, so that the effect of the aperture sieving effect in divalent cation interception is enhanced, and the prepared nanofiltration membrane not only has the advantages of the traditional salt separation nanofiltration membrane, but also has higher water flux and the selectivity of the primary and the divalent ions, and simultaneously has excellent hardness removal capability;

in addition, the surface of the formed polypiperazine amide layer is modified by thiourea dioxide and polyvinyl alcohol, and the modified nanofiltration membrane has excellent chlorine resistance and pollution resistance, and can retain the calcium chloride at a retention rate close to 90% under the chlorination condition of 2000ppm h.

The nanofiltration membrane prepared by the method has the advantages of a desalination nanofiltration membrane and a salt separation nanofiltration membrane, fills up the market blank, is particularly suitable for the field of advanced treatment of municipal drinking water with hard water in a water source area or using underground water as a water source, and has high commercial application value.

Drawings

Fig. 1 is a graph comparing the chlorine resistance of the nanofiltration membranes prepared in example 1, comparative example 4 and comparative example 6 in an acidic environment (pH 4);

figure 2 is a graph comparing the chlorine resistance of the nanofiltration membranes prepared in example 1, comparative example 4 and comparative example 6 in an acidic environment (pH 10);

FIG. 3 is a scanning electron micrograph of the surface of the nanofiltration membrane prepared in example 1 of the present invention;

FIG. 4 is a scanning electron micrograph of a cross section of a nanofiltration membrane prepared in example 1 of the present invention;

FIG. 5 is a scanning electron micrograph of the surface of the nanofiltration membrane prepared in comparative example 1 according to the present invention;

FIG. 6 is a scanning electron micrograph of the cross section of the nanofiltration membrane prepared in comparative example 1 of the present invention.

Detailed Description

The technical solution of the present invention is further described in detail with reference to the following specific examples, but the scope of the present invention is not limited thereto.

First, the main raw material sources adopted in the embodiment of the invention

TABLE 1

Name of raw materials	Parameter index	Manufacturer of the product
			N, N-dimethylformamide	The purity is more than or equal to 99 percent	Hualu constancy
Non-woven fabric	Gram weight of 74g/m2	Sanmu
			Polysulfone	Less than or equal to 0.3 percent of impurities	Solvay
Anhydrous piperazine	The purity is more than or equal to 99 percent	Aladdin reagent
			Trisodium phosphate	The purity is more than or equal to 98 percent	Reagent for treating west longas
Trimesoyl chloride	The purity is more than or equal to 99 percent	Three-strength bennoco
			Vitinone VA64	The purity is more than or equal to 95 percent	Basf-Fr
Thiourea dioxide	The purity is more than or equal to 98 percent	Aladdin reagent
			Polyvinyl alcohol	The purity is more than or equal to 95 percent	Shanxi three-dimensional
Sodium chloride	The purity is more than or equal to 98 percent	Reagent for treating west longas
			Calcium chloride	The purity is more than or equal to 98 percent	Reagent for treating west longas

The performance evaluation method adopted by the nanofiltration membrane for chlorine-resistant and pollution-resistant soft water comprises the following steps:

the separation performance of the prepared nanofiltration membrane is evaluated and mainly characterized by two characteristic parameters, namely the water flux and the salt rejection rate of the membrane.

Water flux (LMH) is defined as: the volume of water per unit time that permeates the active membrane area under certain operating pressure conditions.

Salt rejection calculation formula: r ═ 1-C_p/C_f) × 100%, wherein R represents the retention rate, C_fAnd C_pThe concentrations of the salts (ppm) in the permeate and in the feed, respectively.

The test conditions of the separation performance of the membrane are as follows: the feed solutions were 2000ppm aqueous solutions of magnesium sulfate, sodium chloride and calcium chloride, respectively, with a feed solution temperature of 25 deg.C and an operating pressure of 70psi (0.48 MPa).

The test conditions of the chlorine resistance of the diaphragm are as follows: the membrane subjected to the separation performance test is soaked in a sodium hypochlorite aqueous solution with the pH value of 7.0 and containing 500ppm of active chlorine for 4 hours by adopting a static soaking method, the product (ppm.h) of the concentration of the active chlorine and the soaking time is used as a chlorination strength index, then the membrane subjected to chlorination treatment is repeatedly washed by deionized water, the active chlorine remained in the membrane is completely removed, and finally, the change of the calcium chloride interception performance of the membrane is tested under the test conditions so as to investigate the chlorine resistance of the membrane. In addition, partial membranes are placed in sodium hypochlorite aqueous solutions with different pH values to be soaked for different time, and the chlorine resistance of the membranes is further investigated by testing the change of the calcium chloride interception performance of the membranes.

The anti-pollution performance test conditions of the membrane of the invention are as follows: pure water flux J of 1h recording membrane run at 0.48MPa operating pressure₀Then adding 100ppm sodium alginate and 10ppm calcium chloride as pollutants into the test solution, controlling the temperature at about 25 ℃, and recording the pure water flux J of the membrane after stable operation for 15h_tThe pure water flux attenuation rate of the dyed membrane within 15h is as follows: (1-J)_t/J₀)×100％。