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CN101249385B - A method for purifying amphoteric surfactants by electrodialysis desalination - Google Patents

A method for purifying amphoteric surfactants by electrodialysis desalination Download PDF

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CN101249385B
CN101249385B CN2007101906047A CN200710190604A CN101249385B CN 101249385 B CN101249385 B CN 101249385B CN 2007101906047 A CN2007101906047 A CN 2007101906047A CN 200710190604 A CN200710190604 A CN 200710190604A CN 101249385 B CN101249385 B CN 101249385B
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方云
齐丽云
马娜
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Abstract

一种用电渗析脱盐提纯两性表面活性剂的方法,属于膜分离技术领域。本发明利用两性表面活性剂处于等电点范围时不向两极移动的特性,经电渗析处理后,无机盐小分子进入浓室,两性表面活性剂分子留在淡室,从而将无机盐分离脱除并使两性表面活性剂得以纯化。所适用的两性表面活性剂具有氨基酸或甜菜碱结构或具有咪唑啉型结构。本发明可有效脱除两性表面活性剂中的无机盐,而且分离过程无相变,无污染,成本低,能耗低,一定程度上解决了两性表面活性剂因无机盐提纯困难而限制其发展的问题,并为两性表面活性剂在生产中无机盐的分离提供了经济有效的途径。

The invention discloses a method for purifying amphoteric surfactants by electrodialysis desalination, which belongs to the technical field of membrane separation. The invention utilizes the characteristic that the amphoteric surfactant does not move to the two poles when it is in the range of isoelectric point. After the electrodialysis treatment, the small molecules of the inorganic salt enter the concentrated chamber, and the molecules of the amphoteric surfactant stay in the dilute chamber, thereby separating and removing the inorganic salt. Remove and purify amphoteric surfactants. Suitable amphoteric surfactants have an amino acid or betaine structure or have an imidazoline-type structure. The invention can effectively remove the inorganic salts in the amphoteric surfactants, and the separation process has no phase change, no pollution, low cost and low energy consumption, and solves the limitation of the development of the amphoteric surfactants due to the difficulty in purifying the inorganic salts to a certain extent. problems, and provide an economical and effective way for the separation of inorganic salts in the production of amphoteric surfactants.

Description

一种用电渗析脱盐提纯两性表面活性剂的方法 A method for purifying amphoteric surfactants by electrodialysis desalination

技术领域technical field

一种用电渗析脱盐提纯两性表面活性剂的方法,属于膜分离技术领域。具体地说是一种两性表面活性剂溶液中的无机盐小分子在电场作用下定向运动并选择性透过离子交换膜而与两性表面活性剂分离的方法。The invention discloses a method for purifying amphoteric surfactants by electrodialysis desalination, which belongs to the technical field of membrane separation. Specifically, it is a method in which small inorganic salt molecules in an amphoteric surfactant solution move directionally under the action of an electric field and selectively pass through an ion exchange membrane to separate from the amphoteric surfactant.

背景技术Background technique

两性表面活性剂在同一分子中同时存在不可被电离的正、负电荷中心(或偶极中心),具有低毒和低刺激性,良好的生物降解性,有效的杀菌性及优异的配伍性。在合成两性表面活性剂过程中往往不可避免的产生无机盐小分子,使得产品粘度过高、pH值不稳定或化学稳定性下降等影响两性表面活性剂优异性能的负效应。由于两性表面活性剂的溶解性与无机盐非常相近,使其与无机电解质间的分离非常困难。目前,还没有找到简便经济且分离效果令人满意的方法除去两性表面活性剂中无机盐小分子。Amphoteric surfactants have both non-ionizable positive and negative charge centers (or dipole centers) in the same molecule, and have low toxicity and low irritation, good biodegradability, effective bactericidal properties and excellent compatibility. In the process of synthesizing amphoteric surfactants, small inorganic salt molecules are often unavoidably produced, resulting in negative effects such as high product viscosity, unstable pH value, or decreased chemical stability, which affect the excellent performance of amphoteric surfactants. Since the solubility of amphoteric surfactants is very similar to that of inorganic salts, it is very difficult to separate them from inorganic electrolytes. At present, there is no easy, economical and satisfactory separation method to remove small molecules of inorganic salts in amphoteric surfactants.

电渗析脱盐技术已广泛应用于海水淡化和污水处理过程,具有操作简便、无环境污染、成本低廉且易于实现规模化操作等优点。两性表面活性剂在其等电点时以内盐形式的电中性分子存在,在外电场中既不向阳极移动,也不向阴极移动。如果在所纯化的两性表面活性剂等电点范围内,将含有无机盐杂质的两性表面活性剂溶液作为淡室液,以钠盐如氯化钠或硝酸钠溶液作为浓室初始溶液,氢氧化钠和硫酸溶液分别作为阴、阳极室溶液。调节淡室流量和操作电压进行电渗析,则淡室液中的阴离子如Cl-透过阴膜向阳极迁移而进入浓室,并受到阳膜阻挡留在浓室中;淡室液中阳离子如Na+透过阳膜向阴极方向迁移后也进入浓室,并受到阴膜阻挡被截留在浓室中;而以内盐形式存在的两性表面活性剂在电场作用下不会发生明显迁移留在淡室,从而将无机盐分离脱除并使两性表面活性剂得以纯化。通过控制淡室两性表面活性剂溶液的pH值、淡室流量以及操作电压等操作条件可以使两性表面活性剂在电渗析器中循环脱盐。由于两性表面活性剂水溶性好,不存在膜污染问题,因而可以用电渗析方法进行纯化,目前国内还没有这方面的研究报道。Electrodialysis desalination technology has been widely used in seawater desalination and sewage treatment processes. It has the advantages of simple operation, no environmental pollution, low cost and easy realization of large-scale operation. Amphoteric surfactants exist as electrically neutral molecules in the form of internal salts at their isoelectric points, and neither move to the anode nor to the cathode in an external electric field. If within the isoelectric point range of the purified amphoteric surfactant, the amphoteric surfactant solution containing inorganic salt impurities is used as the weak room solution, and sodium salt such as sodium chloride or sodium nitrate solution is used as the initial solution of the concentrated room, and the hydrogen oxidized Sodium and sulfuric acid solutions are used as the cathode and anode chamber solutions respectively. Adjust the flow rate and operating voltage of the dilute chamber to carry out electrodialysis, and the anions in the dilute chamber liquid such as Cl - migrate to the anode through the negative membrane and enter the concentrated chamber, and are blocked by the positive membrane to stay in the concentrated chamber; the cations in the dilute chamber liquid such as After Na + migrates to the cathode through the positive membrane, it also enters the concentrated chamber, and is blocked by the negative membrane and is trapped in the concentrated chamber; while the amphoteric surfactant in the form of inner salt does not migrate significantly under the action of an electric field and stays in the weak chamber. chamber to separate and remove inorganic salts and to purify amphoteric surfactants. By controlling the operating conditions such as the pH value of the amphoteric surfactant solution in the dilute chamber, the flow rate of the dilute chamber, and the operating voltage, the amphoteric surfactant can be circulated and desalted in the electrodialyzer. Because amphoteric surfactants have good water solubility and no membrane fouling problem, they can be purified by electrodialysis. At present, there is no research report in this area in China.

发明内容Contents of the invention

本发明的目的是针对两性表面活性剂的特点,提出了一种用电渗析脱盐提纯两性表面活性剂的方法,该方法能有效脱除两性表面活性剂中的无机盐,具有在常温、无相变条件下实现物质分离的特点,且成本低,无污染,能耗低,一定程度上解决了两性表面活性剂因无机盐提纯困难而限制其发展的问题。The purpose of the present invention is aimed at the characteristics of amphoteric surfactants, and proposes a method for purifying amphoteric surfactants by electrodialysis desalination, which can effectively remove inorganic salts in amphoteric surfactants, and has The characteristics of material separation under variable conditions, low cost, no pollution, low energy consumption, to a certain extent, solve the problem of limiting the development of amphoteric surfactants due to the difficulty in the purification of inorganic salts.

本发明的技术方案:一种用电渗析提纯两性表面活性剂的方法,在所纯化的两性表面活性剂等电点范围内,将含有无机盐杂质(质量百分含量不超过15%)的两性表面活性剂溶液(质量百分含量不超过35%)作为淡室液,以0.05mol/L的钠盐如氯化钠或硝酸钠溶液1L作为浓室初始溶液,浓度均为0.05mol/L的氢氧化钠和硫酸溶液各1L分别作为阴、阳极室溶液。调节淡室流量为10L/h~40L/h,在操作电压为8V~18V的直流电场作用下,电渗析一段时间,待淡室液的电导率不再降低时停止渗析。Technical scheme of the present invention: a method for purifying amphoteric surfactants by electrodialysis, within the range of the isoelectric point of the purified amphoteric surfactants, amphoteric surfactants containing inorganic salt impurities (mass percentage not exceeding 15%) Surfactant solution (mass percentage content not exceeding 35%) is used as the light room solution, and 0.05mol/L sodium salt such as sodium chloride or sodium nitrate solution 1L is used as the initial solution of the concentrated room, and the concentration is 0.05mol/L. 1L each of sodium hydroxide and sulfuric acid solution was used as the cathode and anode chamber solution respectively. Adjust the flow rate of the dilute chamber to 10L/h to 40L/h. Under the action of a DC electric field with an operating voltage of 8V to 18V, perform electrodialysis for a period of time, and stop dialysis when the conductivity of the dilute chamber liquid no longer decreases.

被纯化的两性表面活性剂具有烷基氨基酸或甜菜碱结构,具有如下通式:The purified amphoteric surfactant has an alkylamino acid or betaine structure with the following general formula:

Figure S2007101906047D00021
Figure S2007101906047D00021

其中R1代表具有8~22个碳原子的烷基或11~25个碳原子的烷基酰胺丙基,R2、R3及R4代表相同或不同的每个具有1~3个碳原子的烷基,M为羧基或磺基;当R2或R3其中至少有一个是氢原子时,即为烷基氨基酸型两性表面活性剂。Wherein R 1 represents an alkyl group having 8 to 22 carbon atoms or an alkylamidopropyl group having 11 to 25 carbon atoms, R 2 , R 3 and R 4 represent the same or different groups each having 1 to 3 carbon atoms The alkyl group, M is carboxyl or sulfo group; when at least one of R 2 or R 3 is a hydrogen atom, it is an alkyl amino acid type amphoteric surfactant.

或被纯化的两性表面活性剂具有咪唑啉型结构,有如下通式:Or the amphoteric surfactant that is purified has imidazoline type structure, has following general formula:

其中R1代表7~21个碳原子的烷基或烯基,R2和R3代表相同或不同的具有1~3个碳原子的亚烷基,X代表氢原子或R3COO-基团。Wherein R 1 represents an alkyl or alkenyl group with 7 to 21 carbon atoms, R 2 and R 3 represent the same or different alkylene groups with 1 to 3 carbon atoms, X represents a hydrogen atom or R 3 COO - group .

本发明的有益效果:Beneficial effects of the present invention:

(1)本发明能有效脱除两性表面活性剂中的无机盐,一定程度上解决了两性表面活性剂因无机盐提纯困难而掩盖其优异性能、并限制其发展的问题,并为两性表面活性剂在生产中无机盐的分离提供了经济有效的途径。(1) The present invention can effectively remove the inorganic salts in the amphoteric surfactants, solve the problem that the amphoteric surfactants cover up their excellent performance and limit their development due to the difficulty in the purification of inorganic salts to a certain extent, and are amphoteric surfactants. The separation of inorganic salts in the production of pharmaceuticals provides a cost-effective way.

(2)电渗析提纯两性表面活性剂具有操作简单、分离过程无相变、无污染、成本低、能耗低且易于实现规模化操作等优点。(2) The purification of amphoteric surfactants by electrodialysis has the advantages of simple operation, no phase change in the separation process, no pollution, low cost, low energy consumption, and easy to realize large-scale operation.

附图说明Description of drawings

图1电渗析装置工作示意图。其中:1、电极;2、膜堆(,

Figure S2007101906047D00023
淡室,口浓室);3、淡室储槽;4、阴极室储槽;5、阳极室储槽;6、浓室储槽;7、泵;8、流量计。Figure 1 Schematic diagram of the working of the electrodialysis device. Among them: 1, electrode; 2, membrane stack (,
Figure S2007101906047D00023
3. Dilute room storage tank; 4. Cathode room storage tank; 5. Anode room storage tank; 6. Concentrated room storage tank; 7. Pump; 8. Flowmeter.

具体实施方式Detailed ways

以下结合图1说明本发明的具体实施方式。A specific embodiment of the present invention will be described below with reference to FIG. 1 .

本发明所使用的电渗析器由50对阴阳离子交换膜组装,膜为磺酸型苯乙烯系和季胺型苯乙烯系异相离子交换膜,单膜的有效膜面积为210mm×65mm。The electrodialyzer used in the present invention is assembled by 50 pairs of anion and cation exchange membranes, the membranes are heterogeneous ion exchange membranes of sulfonic acid type styrene system and quaternary amine type styrene system, and the effective membrane area of a single membrane is 210mm×65mm.

通过以下几组实施例进行说明:Illustrate by following several groups of embodiments:

实施例1 α-癸基甜菜碱溶液的电渗析脱盐The electrodialysis desalination of embodiment 1 α-decyl betaine solution

将含有NaCl的α-癸基甜菜碱溶液调pH值至7.5。测得其中α-癸基甜菜碱及无机盐的质量百分含量分别为10%和3%。将1L上述溶液放入淡室储槽中,以1L 0.05mol/L的NaCl溶液作为浓室初始溶液,分别以1L浓度均为0.05mol/L的氢氧化钠和硫酸溶液各作为阴、阳极室溶液,在10V操作电压,淡室流量为20L/h的操作条件下,对α-癸基甜菜碱溶液进行循环脱盐。待淡室液的电导率不再降低时渗析结束。脱盐率为97%,α-癸基甜菜碱的回收率为82.7%。The pH value of the α-decyl betaine solution containing NaCl was adjusted to 7.5. It is measured that the mass percentages of α-decyl betaine and inorganic salts are 10% and 3% respectively. Put 1L of the above solution into the storage tank of the dilute chamber, use 1L of 0.05mol/L NaCl solution as the initial solution of the concentrated chamber, and use 1L of sodium hydroxide and sulfuric acid solutions with a concentration of 0.05mol/L as the cathode and anode chambers respectively Solution, under the operating conditions of 10V operating voltage and 20L/h flow rate of the dilute chamber, the α-decyl betaine solution is desalted in a cycle. The dialysis ends when the conductivity of the dilute solution no longer decreases. The desalination rate was 97%, and the recovery rate of α-decyl betaine was 82.7%.

实施例2  十二烷基磺丙基甜菜碱溶液的电渗析脱盐Embodiment 2 Electrodialysis desalination of dodecylsulfopropyl betaine solution

将含有未知无机盐的十二烷基磺丙基甜菜碱溶液调pH值至7.2。测得其中十二烷基磺丙基甜菜碱及无机盐的质量百分含量分别为31%和13%。将0.9L上述溶液加0.1L水放入淡室储槽中,以1L 0.05mol/L的NaCl溶液作为浓室初始溶液,分别以浓度均为0.05mol/L的氢氧化钠和硫酸溶液各1L作为阴、阳极室溶液,在14V操作电压,淡室流量为23L/h的操作条件下,对十二烷基磺丙基甜菜碱溶液进行循环脱盐。待淡室液的电导率不再降低时渗析结束。脱盐率为95%,十二烷基磺丙基甜菜碱的回收率为73.6%。Adjust the pH value of the dodecylsulfopropyl betaine solution containing unknown inorganic salt to 7.2. The mass percentages of dodecylsulfopropyl betaine and inorganic salts were measured to be 31% and 13% respectively. Put 0.9L of the above solution plus 0.1L of water into the storage tank of the dilute chamber, use 1L of 0.05mol/L NaCl solution as the initial solution of the concentrated chamber, and use 1L each of sodium hydroxide and sulfuric acid solutions with a concentration of 0.05mol/L As the cathode and anode chamber solutions, the dodecyl sulfopropyl betaine solution is desalted in circulation under the operating conditions of 14V operating voltage and 23L/h dilute chamber flow rate. The dialysis ends when the conductivity of the dilute solution no longer decreases. The desalination rate is 95%, and the recovery rate of dodecyl sulfopropyl betaine is 73.6%.

实施例3  十二酰胺丙基甜菜碱溶液的电渗析脱盐Embodiment 3 Electrodialysis desalination of lauryl amidopropyl betaine solution

将含有未知无机盐的十二酰胺丙基甜菜碱溶液调pH值至6.5,测得其中十二酰胺丙基甜菜碱及无机盐的质量百分含量分别为5%和1%。将1L上述溶液放入淡室储槽中,以1L 0.05mol/L的NaNO3溶液作为浓室初始溶液,以浓度均为0.05mol/L的氢氧化钠和硫酸溶液各1L分别作为阴、阳极室溶液,在8V操作电压,淡室流量为25L/h的操作条件下,对溶液进行循环脱盐。待淡室液的电导率不再降低时渗析结束。脱盐率为97%,十二酰胺丙基甜菜碱的回收率为78.2%。Adjust the pH of the lauryl amidopropyl betaine solution containing unknown inorganic salts to 6.5, and measure the mass percentages of lauryl amidopropyl betaine and inorganic salts to be 5% and 1% respectively. Put 1L of the above solution into the storage tank of the dilute chamber, use 1L of 0.05mol/L NaNO3 solution as the initial solution of the concentrated chamber, and use 1L of sodium hydroxide and sulfuric acid solutions with a concentration of 0.05mol/L as the cathode and anode respectively. Chamber solution, under the operating conditions of 8V operating voltage and dilute chamber flow rate of 25L/h, the solution is desalted in circulation. The dialysis ends when the conductivity of the dilute solution no longer decreases. The desalination rate was 97%, and the recovery rate of lauryl amidopropyl betaine was 78.2%.

实施例4  十六酰胺丙基磺丙基甜菜碱溶液的电渗析脱盐Example 4 Electrodialysis desalination of hexadecanoylaminopropyl sulfopropyl betaine solution

将含有未知无机盐的十六酰胺丙基磺丙基甜菜碱溶液调pH值至7.0。测得其中十六酰胺丙基磺丙基甜菜碱及无机盐的质量百分含量分别为17%和5.5%。将1L上述溶液放入淡室储槽中,以0.05mol/L的NaNO3溶液1L作为浓室初始溶液,以浓度均为0.05mol/L的氢氧化钠和硫酸溶液各1L分别作为阴、阳极室溶液,在10V操作电压,淡室流量为35L/h的操作条件下,对十六酰胺丙基磺丙基甜菜碱溶液进行循环脱盐。待淡室液的电导率不再降低时渗析结束。脱盐率为97%,十六酰胺丙基磺丙基甜菜碱的回收率为85.3%。Adjust the pH of the cetylamidopropylsulfopropylbetaine solution containing the unknown inorganic salt to 7.0. It is measured that the mass percentages of cetylamidopropylsulfopropyl betaine and inorganic salt are 17% and 5.5% respectively. Put 1L of the above solution into the storage tank of the dilute chamber, use 1L of 0.05mol/L NaNO3 solution as the initial solution of the concentrated chamber, and use 1L of sodium hydroxide and sulfuric acid solutions with a concentration of 0.05mol/L as the cathode and anode respectively. Chamber solution, under the operating conditions of 10V operating voltage and 35L/h dilute chamber flow rate, the hexadecanoylaminopropyl sulfopropyl betaine solution is desalted in circulation. The dialysis ends when the conductivity of the dilute solution no longer decreases. The desalination rate was 97%, and the recovery rate of hexadecylamidopropyl sulfopropyl betaine was 85.3%.

实施例5  2-十一烷基-N-羧甲基-N-(2-羟乙基)咪唑啉溶液的电渗析脱盐Example 5 Electrodialysis desalination of 2-undecyl-N-carboxymethyl-N-(2-hydroxyethyl) imidazoline solution

将含有未知无机盐的2-十一烷基-N-羧甲基-N-(2-羟乙基)咪唑啉溶液调pH值至7.0。测得其中2-十一烷基-N-羧甲基-N-(2-羟乙基)咪唑啉及无机盐的质量百分含量分别为31%和8.0%。将1L上述溶液放入淡室储槽中,以0.05mol/L的NaCl溶液1L作为浓室初始溶液,浓度均为0.05mol/L的氢氧化钠和硫酸溶液各1L分别作为阴、阳极室溶液,在18V操作电压,淡室流量为25L/h的操作条件下,对2-十一烷基-N-羧甲基-N-(2-羟乙基)咪唑啉溶液进行循环脱盐。待淡室液的电导率不再降低时渗析结束。脱盐率为95%,2-十一烷基-N-羧甲基-N-(2-羟乙基)咪唑啉的回收率为76.4%。Adjust the pH value of the 2-undecyl-N-carboxymethyl-N-(2-hydroxyethyl)imidazoline solution containing an unknown inorganic salt to 7.0. The mass percentages of 2-undecyl-N-carboxymethyl-N-(2-hydroxyethyl)imidazoline and inorganic salts were measured to be 31% and 8.0%, respectively. Put 1 L of the above solution into the storage tank of the dilute chamber, use 1 L of 0.05 mol/L NaCl solution as the initial solution of the concentrated chamber, and 1 L of sodium hydroxide and sulfuric acid solutions with a concentration of 0.05 mol/L as the cathode and anode chamber solutions respectively , under the operating conditions of 18V operating voltage and 25L/h dilute chamber flow rate, the 2-undecyl-N-carboxymethyl-N-(2-hydroxyethyl) imidazoline solution was desalted in circulation. The dialysis ends when the conductivity of the dilute solution no longer decreases. The desalination rate was 95%, and the recovery rate of 2-undecyl-N-carboxymethyl-N-(2-hydroxyethyl)imidazoline was 76.4%.

实施例6  N-十二烷基-β-氨基丙酸钠溶液的电渗析脱盐Example 6 Electrodialysis desalination of N-dodecyl-β-alanine sodium solution

将含有未知无机盐的N-十二烷基-β-氨基丙酸钠溶液调pH值至7.0。测得其中N-十二烷基-β-氨基丙酸钠及无机盐的质量百分含量分别为30%和5.6%。将1L上述溶液放入淡室储槽中,以1L 0.05mol/L的NaNO3溶液作为浓室初始溶液,浓度均为0.05mol/L的氢氧化钠和硫酸溶液各1L分别作为阴、阳极室溶液,在18V操作电压,淡室流量为20L/h的操作条件下,对N-十二烷基-β-氨基丙酸钠溶液进行循环脱盐。待淡室液的电导率不再降低时渗析结束。脱盐率为95%,N-十二烷基-β-氨基丙酸钠的回收率为76.4%。Adjust the pH of the sodium N-dodecyl-β-alanine solution containing the unknown inorganic salt to 7.0. The mass percentages of N-dodecyl-β-alanine sodium and inorganic salts were measured to be 30% and 5.6% respectively. Put 1L of the above solution into the storage tank of the dilute chamber, use 1L of 0.05mol/L NaNO3 solution as the initial solution of the concentrated chamber, and 1L each of sodium hydroxide and sulfuric acid solutions with a concentration of 0.05mol/L as the cathode and anode chambers respectively solution, under the operating conditions of 18V operating voltage and 20L/h dilute chamber flow rate, the N-dodecyl-β-alanine sodium solution is desalted in circulation. The dialysis ends when the conductivity of the dilute solution no longer decreases. The desalination rate was 95%, and the recovery rate of sodium N-dodecyl-β-alanine was 76.4%.

Claims (4)

1. method with electrodialysis desalination purifying ampholytic surfactant, it is characterized in that in purified amphoteric surfactant isoelectric point scope, the amphoteric surfactant solution that will contain inorganic salts impurity is as light chamber liquid, the quality percentage composition of inorganic salts is no more than 15% in the liquid of light chamber, the quality percentage composition of surfactant is no more than 35%, with the sodium salt solution 1L of 0.05mol/L as dense chamber initial soln, concentration is the NaOH of 0.05mol/L and each 1L of sulfuric acid solution respectively as cloudy, anode chamber's solution, regulating light chamber flow is 10L/h~40L/h, be to carry out electrodialysis desalination under the DC electric field effect of 8V~18V at operating voltage, dialysis finished when the electrical conductivity for the treatment of light chamber liquid no longer reduced.
2. according to the method for the described electrodialysis desalination purifying ampholytic of claim 1 surfactant, it is characterized in that the used sodium salt solution in dense chamber is sodium chloride or sodium nitrate.
3. the application of the described electrodialysis desalination purifying ampholytic of claim 1 surface-active agent method is characterized in that the amphoteric surfactant that is purified has betaine structure, has following general formula:
R wherein 1Representative has the alkyl of 8~22 carbon atoms or the alkylamide propyl of 11~25 carbon atoms, R 2, R 3And R 4Represent identical or different each to have the alkyl of 1~3 carbon atom, M is carboxyl or sulfo group.
4. the application of the described electrodialysis desalination purifying ampholytic of claim 1 surface-active agent method is characterized in that the amphoteric surfactant that this process is fit to be purified equally has the imidazoline type structure, has following general formula:
R wherein 1Represent the alkyl or alkenyl of 7~21 carbon atoms, R 2And R 3Represent the identical or different alkylidene with 1~3 carbon atom, X represents hydrogen atom or R 3COO -Group.
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Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1525692A (en) * 1974-09-06 1978-09-20 Albright & Wilson Surfactant purification by an electrolytic method
EP0736521A1 (en) * 1995-04-05 1996-10-09 Rhone-Poulenc Chimie Process for the purification of amphoteric surfactants through electrodialysis
EP0982283A2 (en) * 1998-08-24 2000-03-01 Degussa-Hüls Aktiengesellschaft Method for the separation of polyfunctional alcohols from water-soluble salts in aqueous systems
CN1387458A (en) * 1999-11-03 2002-12-25 巴斯福股份公司 Method for purification of amino acid contg. solutions by electrodialysis
CN1444503A (en) * 2000-08-11 2003-09-24 大金工业株式会社 Method of recovering fluorochemical surfactant

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1525692A (en) * 1974-09-06 1978-09-20 Albright & Wilson Surfactant purification by an electrolytic method
EP0736521A1 (en) * 1995-04-05 1996-10-09 Rhone-Poulenc Chimie Process for the purification of amphoteric surfactants through electrodialysis
EP0982283A2 (en) * 1998-08-24 2000-03-01 Degussa-Hüls Aktiengesellschaft Method for the separation of polyfunctional alcohols from water-soluble salts in aqueous systems
CN1387458A (en) * 1999-11-03 2002-12-25 巴斯福股份公司 Method for purification of amino acid contg. solutions by electrodialysis
CN1444503A (en) * 2000-08-11 2003-09-24 大金工业株式会社 Method of recovering fluorochemical surfactant

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