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CN1954901A - Polyester amide reverse osmosis composite membrane and preparation method thereof - Google Patents

Polyester amide reverse osmosis composite membrane and preparation method thereof Download PDF

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CN1954901A
CN1954901A CN 200510104327 CN200510104327A CN1954901A CN 1954901 A CN1954901 A CN 1954901A CN 200510104327 CN200510104327 CN 200510104327 CN 200510104327 A CN200510104327 A CN 200510104327A CN 1954901 A CN1954901 A CN 1954901A
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reverse osmosis
composite membrane
osmosis composite
polyester amide
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CN100484615C (en
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王铎
娄红瑞
高从堦
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Ocean University of China
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Abstract

A composite reverse osmosis polyester-amide membrane is composed of a porous supporting layer, and a compact polyester-amide surface layer prepared by interface polymerization between aminoglucose or aminobiglucose or the mixture of aminoglucose and metaphenyldiamine and the polyatomic acyl chloride. Its preparing process includes such steps as immersing the one surface of polysulfone film in the aqueous solution of amino monomer, dripdrying, interface polymerization reaction on the solution of polyatomic acyl chloride, drying, heat treating and rinsing in deionized water. It has high water throughput.

Description

聚酯酰胺反渗透复合膜及其制备方法Polyester amide reverse osmosis composite membrane and preparation method thereof

技术领域technical field

本发明涉及一种反渗透复合膜及其制备方法,具体的说是一种聚酯酰胺反渗透复合膜及其制备方法。The invention relates to a reverse osmosis composite membrane and a preparation method thereof, in particular to a polyester amide reverse osmosis composite membrane and a preparation method thereof.

背景技术Background technique

反渗透作为目前世界上最先进的膜分离技术之一,具有净化率高、成本低等优点,被广泛应用于海水和苦咸水淡化、纯水和超纯水制备、工业用水处理、废水资源化等领域。反渗透膜是反渗透技术的核心。1960年,美国加利福尼亚大学的Loeb和Sourirajan等首次制成了世界上具有历史意义的高脱盐(98.6%)、高通量(10.1MPa下259L/d·m2)的非对称醋酸纤维反渗透膜,大大地促进了反渗透膜技术的发展。1978年,美国J.E.Cadotte等学者在反渗透复合膜制备技术和功能材料研究方面取得重大突破,研究开发出了第一代芳香聚酰胺反渗透复合膜,与醋酸纤维素相比,具有脱盐率高、通量大、操作压力要求低等优点。反渗透复合膜是将超薄的功能性皮层材料经不同方法负载于多孔支撑体上而形成的。而膜材料和支撑体可以分别选择,因而有利于实现膜性能最优化。1980年美国Filmtec公司推出了FT-30高性能反渗透复合膜,实现了反渗透复合膜技术的商品化,从而使反渗透复合膜技术取得了划时代的进步。As one of the most advanced membrane separation technologies in the world, reverse osmosis has the advantages of high purification rate and low cost, and is widely used in desalination of seawater and brackish water, preparation of pure water and ultrapure water, industrial water treatment, waste water resources chemical and other fields. Reverse osmosis membrane is the core of reverse osmosis technology. In 1960, Loeb and Sourirajan of the University of California made the world's historic high desalination (98.6%), high flux (259L/d·m 2 under 10.1MPa) asymmetric cellulose acetate reverse osmosis membrane , greatly promoted the development of reverse osmosis membrane technology. In 1978, scholars such as JECadotte in the United States made a major breakthrough in the preparation technology of reverse osmosis composite membranes and research on functional materials. They researched and developed the first generation of aromatic polyamide reverse osmosis composite membranes. It has the advantages of large flux and low operating pressure requirements. The reverse osmosis composite membrane is formed by loading ultra-thin functional skin materials on porous supports through different methods. The membrane material and support can be selected separately, which is conducive to the optimization of membrane performance. In 1980, the American Filmtec company launched the FT-30 high-performance reverse osmosis composite membrane, which realized the commercialization of the reverse osmosis composite membrane technology, thus making the reverse osmosis composite membrane technology an epoch-making progress.

芳香族聚酰胺膜脱盐率高、通量大,耐生物降解,且机械、热和化学稳定性好,是目前世界上两大最主要的反渗透膜之一,但其耐氧化、抗污染能力较差。目前,通常采用对膜面进行改性、开发新型聚合单体和聚合工艺来提高芳香族聚酰胺反渗透复合膜的抗氧化性。日本的Nitto Denko公司于1997年推出的耐污染型低压反渗透复合膜LF10系列就是在传统的芳香聚酰胺膜表面复合上一层PVA,既减弱了膜表面的负电性又提高了膜的亲水性和耐氯性。但在膜面上进行改性容易导致膜水通量降低。Kim等用多元胺和多元酚混合再与多元酰氯溶液进行单面界面聚合,即在聚酰胺中引入酯功能键,使其耐氯性能大大改善。但脱盐率和水通量等其他性能并不理想。Aromatic polyamide membrane has high desalination rate, large flux, biodegradation resistance, and good mechanical, thermal and chemical stability. It is currently one of the two most important reverse osmosis membranes in the world, but its oxidation resistance and anti-pollution ability poor. At present, the oxidation resistance of aromatic polyamide reverse osmosis composite membranes is usually improved by modifying the membrane surface and developing new polymer monomers and polymerization processes. The pollution-resistant low-pressure reverse osmosis composite membrane LF10 series launched by Japan's Nitto Denko in 1997 is to compound a layer of PVA on the surface of the traditional aromatic polyamide membrane, which not only weakens the negative charge of the membrane surface but also improves the hydrophilicity of the membrane. and chlorine resistance. However, modification on the membrane surface can easily lead to a decrease in membrane water flux. Kim et al. mixed polyamine and polyphenol and then carried out single-sided interfacial polymerization with polyacyl chloride solution, that is, introduced ester functional bonds into polyamide, which greatly improved its chlorine resistance. But other properties such as salt rejection and water flux are not ideal.

发明内容Contents of the invention

针对上述问题,本发明的目的是提供一种高脱盐率、高通量、耐氧化的聚酯酰胺反渗透复合膜,并提供其制备方法。In view of the above problems, the object of the present invention is to provide a polyester amide reverse osmosis composite membrane with high desalination rate, high flux, and oxidation resistance, and to provide a preparation method thereof.

本发明的聚酯酰胺反渗透复合膜包括一层多孔的支撑层和一层致密的聚酯酰胺分离皮层。The polyester amide reverse osmosis composite membrane of the invention comprises a porous support layer and a dense polyester amide separation skin layer.

所述多孔的支撑层可以为聚砜、聚醚砜、磺化聚砜或磺化聚醚砜;The porous support layer may be polysulfone, polyethersulfone, sulfonated polysulfone or sulfonated polyethersulfone;

所述聚酯酰胺分离皮层由氨基葡萄糖、氨基葡萄二糖或氨基葡萄糖和间苯二胺的混合物与多元酰氯通过界面聚合得到;The polyester amide separation cortex is obtained by interfacial polymerization of glucosamine, glucosamine or a mixture of glucosamine and m-phenylenediamine and polyacyl chlorides;

所述聚酯酰胺分离皮层的厚度在50~200nm之间。The thickness of the polyester amide separation skin layer is between 50nm and 200nm.

聚酯酰胺反渗透复合膜的制备方法,包括以下步骤:The preparation method of polyester amide reverse osmosis composite membrane comprises the following steps:

(1)将聚砜支撑膜单面浸入2%的氨基单体的水溶液;(1) Immerse one side of the polysulfone support membrane in an aqueous solution of 2% amino monomer;

(2)待表面沥干后,与0.1~0.2%多元酰氯溶液进行界面聚合反应;(2) After the surface is drained, carry out interfacial polymerization reaction with 0.1~0.2% polyacyl chloride solution;

(3)在空气中干燥1~5分钟;(3) Dry in the air for 1 to 5 minutes;

(4)50~100℃热处理3~10分钟;(4) Heat treatment at 50-100°C for 3-10 minutes;

(5)去离子水漂洗,制得反渗透复合膜。(5) Rinse with deionized water to prepare a reverse osmosis composite membrane.

反渗透复合膜性能测试:Reverse osmosis composite membrane performance test:

在浓度为20000mg/L的氯化钠水溶液、操作压力1.6MPa、温度25℃的条件下测试膜的性能。脱盐率(R)和水通量(J)计算公式分别为:The performance of the membrane was tested under the conditions of a sodium chloride aqueous solution with a concentration of 20000 mg/L, an operating pressure of 1.6 MPa, and a temperature of 25 °C. The calculation formulas of salt rejection rate (R) and water flux (J) are:

Figure A20051010432700041
Figure A20051010432700041

Figure A20051010432700042
Figure A20051010432700042

具体实施方式Detailed ways

下面结合具体实施例来进一步说明本发明。The present invention will be further described below in conjunction with specific examples.

实施例1Example 1

2%(wt%)氨基葡萄糖和0.1%(wt%)十二烷基硫酸钠配成水相溶液,用氢氧化钠调节pH=12;将均苯三甲酰氯(TMC)溶于正己烷中配成0.1%(wt%)有机相溶液。使聚砜支撑膜单面浸入2%的水相溶液中,时间3分钟;沥去多余水溶液,与有机相进行反应30秒;沥去有机相,并在空气中干燥1分钟;在鼓风干燥箱中于75℃热处理3分钟;去离子水漂洗,制得反渗透复合膜。2% (wt %) glucosamine and 0.1% (wt %) sodium lauryl sulfate are made into water phase solution, adjust pH=12 with sodium hydroxide; Dissolve trimesoyl chloride (TMC) in n-hexane and prepare Into a 0.1% (wt%) organic phase solution. Immerse one side of the polysulfone support membrane in 2% aqueous phase solution for 3 minutes; drain the excess aqueous solution and react with the organic phase for 30 seconds; drain the organic phase and dry it in the air for 1 minute; Heat treatment at 75° C. for 3 minutes in an oven; rinse with deionized water to prepare a reverse osmosis composite membrane.

将上面制得的反渗透复合膜干燥,用衰减全反射傅立叶红外光谱仪测其红外吸收。结果发现:1663cm-1、1540cm-1处有吸收,分别为酰胺I带和酰胺II带特征峰特征峰,证明了酰胺键的生成。1013cm-1处C6羟基的吸收峰消失,同时在1540cm-1出现了酯基C-O-C的吸收峰,证明了酯基的生成。The reverse osmosis composite membrane prepared above was dried, and its infrared absorption was measured with an attenuated total reflection Fourier transform infrared spectrometer. The results showed that there were absorptions at 1663cm -1 and 1540cm -1 , which were characteristic peaks of amide I band and amide II band respectively, which proved the formation of amide bonds. The absorption peak of C 6 hydroxyl group at 1013cm -1 disappeared, and the absorption peak of ester group COC appeared at 1540cm -1 , which proved the formation of ester group.

实施例2Example 2

按照与实施例1相同的步骤,制备反渗透复合膜。水相组成为:1.2%(wt%)间苯二胺、0.8%(wt%)氨基葡萄糖和0.1%(wt%)十二烷基硫酸钠,用氢氧化钠调节pH=12;有机相为0.1%(wt%)的TMC溶于正己烷中配成;使聚砜支撑膜单面浸入水相溶液中,时间3分钟;沥去多余水溶液,与有机相进行反应60秒;沥去有机相,并在空气中干燥3分钟;在鼓风干燥箱中于85℃热处理5分钟;去离子水漂洗,制得反渗透复合膜。Following the same steps as in Example 1, a reverse osmosis composite membrane was prepared. The aqueous phase consists of: 1.2% (wt%) m-phenylenediamine, 0.8% (wt%) glucosamine and 0.1% (wt%) sodium lauryl sulfate, and adjust pH=12 with sodium hydroxide; the organic phase is 0.1% (wt%) TMC is dissolved in n-hexane and is formulated; the polysulfone support membrane is immersed in the aqueous phase solution on one side for 3 minutes; the excess aqueous solution is drained, and the organic phase is reacted for 60 seconds; the organic phase is drained , and dried in air for 3 minutes; heat treated in a blast drying oven at 85° C. for 5 minutes; rinsed with deionized water to prepare a reverse osmosis composite membrane.

按照前面所述的方法,测定其性能。在浓度为20000mg/L的氯化钠水溶液、操作压力1.6MPa、温度25℃下,通量为29.3L/m2·h,脱盐率为98.0。According to the method described above, its performance was measured. In an aqueous sodium chloride solution with a concentration of 20,000 mg/L, an operating pressure of 1.6 MPa, and a temperature of 25°C, the flux is 29.3 L/m 2 ·h, and the desalination rate is 98.0.

实施例3Example 3

按照与实施例1相同的步骤,制备反渗透复合膜。水相组成为:1.2%(wt%)间苯二胺、0.8%(wt%)氨基葡萄糖和0.1%(wt%)十二烷基硫酸钠,用氢氧化钠调节pH=12;有机相为0.2%(wt%)的TMC溶于C12溶剂油中配成;使聚砜支撑膜单面浸入水相溶液中,时间3分钟;沥去多余水溶液,与有机相进行反应60秒;沥去有机相,并在空气中干燥5分钟;在鼓风干燥箱中于85℃热处理10分钟;去离子水漂洗,制得反渗透复合膜。Following the same steps as in Example 1, a reverse osmosis composite membrane was prepared. The aqueous phase consists of: 1.2% (wt%) m-phenylenediamine, 0.8% (wt%) glucosamine and 0.1% (wt%) sodium lauryl sulfate, and adjust pH=12 with sodium hydroxide; the organic phase is The TMC of 0.2% (wt%) is dissolved in C 12 mineral spirits and is made up; The polysulfone supporting membrane is immersed in the water phase solution on one side, time 3 minutes; Drain excess aqueous solution, react with organic phase for 60 seconds; Drain organic phase, and dried in the air for 5 minutes; heat-treated in a blast oven at 85° C. for 10 minutes; rinsed with deionized water to prepare a reverse osmosis composite membrane.

按照前面所述的方法,测定其性能。在浓度为20000mg/L的氯化钠水溶液、操作压力1.6MPa、温度25℃下,通量为20.9L/m2·h,脱盐率为98.6。According to the method described above, its performance was measured. In an aqueous sodium chloride solution with a concentration of 20,000 mg/L, an operating pressure of 1.6 MPa, and a temperature of 25°C, the flux is 20.9 L/m 2 ·h, and the desalination rate is 98.6.

对比例1Comparative example 1

按照与实施例1相同的步骤,制备反渗透复合膜。先将2%(wt%)三乙胺溶于去离子水中,用盐酸调节pH=8;再将2%(wt%)间苯二胺和0.1%(wt%)十二烷基硫酸钠溶于其中配成水相;有机相为0.2%(wt%)的TMC溶于C12溶剂油中配成;使聚砜支撑膜单面浸入水相溶液中,时间3分钟;沥去多余水溶液,与有机相进行反应30秒;沥去有机相,并在空气中干燥1分钟;在鼓风干燥箱中于75℃热处理10分钟;去离子水漂洗,制得反渗透复合膜。Following the same steps as in Example 1, a reverse osmosis composite membrane was prepared. First 2% (wt%) triethylamine was dissolved in deionized water, and the pH=8 was adjusted with hydrochloric acid; then 2% (wt%) m-phenylenediamine and 0.1% (wt%) sodium lauryl sulfate were dissolved Make water phase therein; The TMC that organic phase is 0.2% (wt%) is dissolved in C 12 solvent naphtha and is made into; Make polysulfone support membrane one-sided immersion in the water phase solution, time 3 minutes; Drain excess aqueous solution, React with the organic phase for 30 seconds; drain the organic phase and dry in the air for 1 minute; heat treat in a blast drying oven at 75° C. for 10 minutes; rinse with deionized water to prepare a reverse osmosis composite membrane.

按照前面所述的方法,测定其性能。在浓度为20000mg/L的氯化钠水溶液、操作压力1.6MPa、温度25℃下,通量为15.4L/m2·h,脱盐率为98.1。According to the method described above, its performance was determined. In an aqueous sodium chloride solution with a concentration of 20,000 mg/L, an operating pressure of 1.6 MPa, and a temperature of 25°C, the flux is 15.4 L/m 2 ·h, and the desalination rate is 98.1.

实施例4Example 4

将实施例3和对比例1所制备的反渗透复合膜,在含1000ppm有效氯的次氯酸钠溶液中浸泡5小时,取出,用去离子洗涤。在浓度为20000mg/L的氯化钠水溶液、操作压力1.6MPa、温度25℃下,测定其通量和脱盐率。The reverse osmosis composite membranes prepared in Example 3 and Comparative Example 1 were immersed in a sodium hypochlorite solution containing 1000 ppm available chlorine for 5 hours, taken out, and washed with deionization. The flux and desalination rate were measured in an aqueous sodium chloride solution with a concentration of 20000mg/L, an operating pressure of 1.6MPa, and a temperature of 25°C.

结果如表1所示:The results are shown in Table 1:

              表1  反渗透复合膜的耐氧化性实验结果  膜序号   初始性能   经5000ppm·h次氯酸钠处理后的性能   R(%)   J(L/m2·h)   R(%)   J(L/m2·h)  实施例3   98.6   20.9   97.6   23.2  对比例1   98.1   15.4   93.7   27.9 Table 1 Oxidation resistance test results of reverse osmosis composite membranes Membrane serial number initial performance Performance after treatment with 5000ppm·h sodium hypochlorite R(%) J(L/m 2 ·h) R(%) J(L/m 2 ·h) Example 3 98.6 20.9 97.6 23.2 Comparative example 1 98.1 15.4 93.7 27.9

从上述实验结果中可以看出,在同样具有高脱盐率(>98%)的情况下,聚酯酰胺反渗透复合膜比芳香聚酰胺反渗透复合膜具有更高的水通量;而且耐氯的氧化性也更好。As can be seen from the above experimental results, in the case of the same high desalination rate (> 98%), the polyester amide reverse osmosis composite membrane has a higher water flux than the aromatic polyamide reverse osmosis composite membrane; and chlorine resistance Oxidation is also better.

Claims (5)

1.一种聚酯酰胺反渗透复合膜,其特征在于它包括一层多孔的支撑层和一层致密的聚酯酰胺分离皮层。1. a polyester amide reverse osmosis composite membrane is characterized in that it comprises a porous support layer and a dense polyester amide separation cortex. 2.根据权利要求1所述的反渗透复合膜,其特征在于所述的多孔支撑层可以为聚砜、聚醚砜、磺化聚砜或磺化聚醚砜。2. The reverse osmosis composite membrane according to claim 1, characterized in that the porous support layer can be polysulfone, polyethersulfone, sulfonated polysulfone or sulfonated polyethersulfone. 3.根据权利要求1所述的反渗透复合膜,其特征在于所述的聚酯酰胺分离皮层由氨基葡萄糖、氨基葡萄二糖或氨基葡萄糖和间苯二胺的混合物与多元酰氯通过界面聚合得到。3. reverse osmosis composite membrane according to claim 1, is characterized in that described polyester amide separation cortex is obtained by interfacial polymerization by the mixture of glucosamine, glucosamine or glucosamine and m-phenylenediamine and polyacyl chloride . 4.根据权利要求1或3所述的反渗透复合膜,其特征在于所述聚酯酰胺分离皮层的厚度在50~200nm之间。4. The reverse osmosis composite membrane according to claim 1 or 3, characterized in that the thickness of the polyester amide separation skin layer is between 50-200 nm. 5.根据权利1所述聚酯酰胺反渗透复合膜的制备方法,包括以下步骤:5. according to the preparation method of the described polyester amide reverse osmosis composite membrane of right 1, comprise the following steps: (1)将聚砜支撑膜单面浸入2%氨基单体的水溶液;(1) Immerse one side of the polysulfone support membrane in an aqueous solution of 2% amino monomer; (2)待表面沥干后,与0.1~0.2%多元酰氯溶液进行界面聚合反应;(2) After the surface is drained, carry out interfacial polymerization reaction with 0.1~0.2% polyacyl chloride solution; (3)在空气中干燥1~5分钟;(3) Dry in the air for 1 to 5 minutes; (4)50~100℃热处理3~10分钟;(4) Heat treatment at 50-100°C for 3-10 minutes; (5)去离子水漂洗,制得反渗透复合膜。(5) Rinse with deionized water to prepare a reverse osmosis composite membrane.
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CN102258948A (en) * 2011-05-31 2011-11-30 南京帝膜净水材料开发有限公司 Method for preparing polyamide reverse osmosis compound membrane
CN102527265A (en) * 2010-12-15 2012-07-04 华东理工大学 Membrane functional monomer containing hexafluoroisopropanol group and nanofiltration membrane preparation method thereof
CN103331110A (en) * 2013-05-27 2013-10-02 天津工业大学 Pollution-resistant chlorine polyamide-resistant reverse osmosis composite membrane and preparation method thereof
CN105032201A (en) * 2009-08-24 2015-11-11 Oasys水有限公司 Forward osmosis membranes
CN111788251A (en) * 2018-06-15 2020-10-16 株式会社Lg化学 Composition for interfacial polymerization of polyamide and method for producing water treatment separation membrane by using the same
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CN102527265A (en) * 2010-12-15 2012-07-04 华东理工大学 Membrane functional monomer containing hexafluoroisopropanol group and nanofiltration membrane preparation method thereof
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CN111788251A (en) * 2018-06-15 2020-10-16 株式会社Lg化学 Composition for interfacial polymerization of polyamide and method for producing water treatment separation membrane by using the same
CN111788251B (en) * 2018-06-15 2023-03-28 株式会社Lg化学 Composition for interfacial polymerization of polyamide and method for manufacturing water treatment separation membrane by using the same
US11992812B2 (en) 2018-06-15 2024-05-28 Lg Chem, Ltd. Composition for polyamide interfacial polymerization, and method for manufacturing water treatment separation membrane by using same
EP3708603B1 (en) * 2018-06-15 2025-03-12 Lg Chem, Ltd. Composition for polyamide interfacial polymerization, and method for manufacturing water treatment separation membrane by using same
CN115228300A (en) * 2022-06-24 2022-10-25 河北工业大学 An ion-selective nanofiltration membrane and its preparation method and application
CN115228300B (en) * 2022-06-24 2024-02-23 河北工业大学 Ion-selective nanofiltration membrane and preparation method and application thereof
CN118477497A (en) * 2024-06-11 2024-08-13 浙江奥氏芯材科技有限公司 Preparation method of salt lake lithium extraction reverse osmosis membrane

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