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CN108927015A - A kind of preparation method of big flux ultrafiltration membrane - Google Patents

A kind of preparation method of big flux ultrafiltration membrane Download PDF

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CN108927015A
CN108927015A CN201810940214.5A CN201810940214A CN108927015A CN 108927015 A CN108927015 A CN 108927015A CN 201810940214 A CN201810940214 A CN 201810940214A CN 108927015 A CN108927015 A CN 108927015A
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kaolin
ultrafiltration membrane
membrane
preparation
solution
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刘婷
周慧敏
孙克宁
刘晓燕
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Beijing Institute of Technology BIT
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    • 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
    • B01D71/44Polymers obtained by reactions only involving carbon-to-carbon unsaturated bonds, not provided for in a single one of groups B01D71/26-B01D71/42
    • 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
    • B01D67/0079Manufacture of membranes comprising organic and inorganic components
    • 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

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  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

本发明提供了一种大通量超滤膜的制备方法,包括如下步骤:高岭土与饱和的尿素溶液搅拌均匀,烘干得到插层复合物,插层复合物加入到HCl溶液中进行超声,得到高岭土纳米片溶液;高岭土纳米片溶液用PH调节剂调节至PH>9,获得高岭土纳米片分散液;将得到的高岭土纳米片分散液与阳离子聚丙烯酰胺,通过层层堆叠的方法将高岭土纳米片负载到醋酸纤维素微滤膜表面。本发明制备的高岭土超滤膜其初始通量是聚偏二氟乙烯超滤膜初始通量的十倍,大大降低膜通量的衰减,减少膜污染,提高了使用寿命,提高水处理效率,提高了高岭土超滤膜在水中的稳定性,方法简单易操作且易于规模化使用,利于推广。The invention provides a method for preparing a large-flux ultrafiltration membrane, comprising the following steps: kaolin and saturated urea solution are evenly stirred, dried to obtain an intercalation compound, and the intercalation compound is added to HCl solution for ultrasonication to obtain Kaolin nano-sheet solution; the kaolin nano-sheet solution is adjusted to PH>9 with a pH regulator to obtain a kaolin nano-sheet dispersion; the obtained kaolin nano-sheet dispersion and cationic polyacrylamide are stacked to form a kaolin nano-sheet loaded onto the surface of a cellulose acetate microfiltration membrane. The initial flux of the kaolin ultrafiltration membrane prepared by the present invention is ten times that of the polyvinylidene fluoride ultrafiltration membrane, which greatly reduces the attenuation of the membrane flux, reduces membrane pollution, improves the service life, and improves the water treatment efficiency. The stability of the kaolin ultrafiltration membrane in water is improved, the method is simple, easy to operate and easy to use on a large scale, and is beneficial to popularization.

Description

一种大通量超滤膜的制备方法A kind of preparation method of large flux ultrafiltration membrane

技术领域technical field

本发明属于超滤膜技术领域,尤其是涉及一种大通量超滤膜的制备方法。The invention belongs to the technical field of ultrafiltration membranes, and in particular relates to a preparation method of a large flux ultrafiltration membrane.

背景技术Background technique

膜技术是一种简便高效的水处理技术,在环保水处理领域的应用越来越广泛,并逐步成为世界可持续发展战略的基础之一。膜技术以其广泛的适用性被广泛应用于各个领域的水处理。然而,膜制备过程的复杂性和高成本是膜技术推广应用的一个重要障碍。能用于制备薄膜的材料有很多,其中以无机、陶瓷材料和有机、聚合物材料最为主要。由于无机、陶瓷材料用于制备薄膜时成本比较高且脆性大,机械强度小,所以近几年有机、聚合物材料被广泛用于制备薄膜且被用于处理表面水中的天然有机物。例如,近几年氧化石墨烯和聚偏二氟乙烯被广泛用于制备稳定的微滤膜、超滤膜、纳滤膜来处理水中的天然有机物。然而该制备过程复杂、成本高、且不环保。所以寻找新材料或者新的制备方法来降低成本和简化制备过程势在必行。Membrane technology is a simple and efficient water treatment technology. It is widely used in the field of environmental protection water treatment and has gradually become one of the foundations of the world's sustainable development strategy. Membrane technology is widely used in water treatment in various fields due to its wide applicability. However, the complexity and high cost of the membrane preparation process is an important obstacle to the promotion and application of membrane technology. There are many materials that can be used to prepare thin films, among which inorganic and ceramic materials and organic and polymer materials are the most important. Due to the high cost, high brittleness and low mechanical strength of inorganic and ceramic materials used to prepare thin films, organic and polymer materials have been widely used to prepare thin films and treat natural organic matter in surface water in recent years. For example, in recent years, graphene oxide and polyvinylidene fluoride have been widely used to prepare stable microfiltration membranes, ultrafiltration membranes, and nanofiltration membranes to treat natural organic matter in water. However, the preparation process is complex, costly and not environmentally friendly. Therefore, it is imperative to find new materials or new preparation methods to reduce costs and simplify the preparation process.

发明内容Contents of the invention

有鉴于此,本发明旨在提出一种大通量超滤膜的制备方法,制备方法简单,成本低且具有较好的过滤效果,使用寿命长。In view of this, the present invention aims to propose a method for preparing a large-flux ultrafiltration membrane, which is simple, low in cost, has good filtering effect and long service life.

为达到上述目的,本发明的技术方案是这样实现的:In order to achieve the above object, technical solution of the present invention is achieved in that way:

一种大通量超滤膜的制备方法,包括如下步骤:A method for preparing a large flux ultrafiltration membrane, comprising the steps of:

步骤一:高岭土与饱和的尿素溶液在55-70℃下用分散机在200r的转速下搅拌80h,烘干得到插层复合物,插层复合物加入到HCl溶液中进行超声,得到高岭土纳米片溶液;Step 1: Stir kaolin and saturated urea solution at 55-70°C with a disperser at a speed of 200r for 80 hours, dry to obtain an intercalation compound, add the intercalation compound to HCl solution for ultrasonication, and obtain kaolin nanosheets solution;

步骤二:高岭土纳米片溶液用PH调节剂调节至PH>9,以使高岭土纳米片带上负电从而增加纳米片之间的斥力防止剥离所得的纳米片再重新聚集,之后再用高速搅拌机进行搅拌五分钟,由于高岭土纳米片的吸附作用一段时间后溶液的PH会降低,所以之后需重新调节PH>9,再用高速搅拌机进行搅拌五分钟,获得高岭土纳米片分散液;Step 2: The kaolin nanosheet solution is adjusted to PH>9 with a pH regulator, so that the kaolin nanosheet is negatively charged to increase the repulsion between the nanosheets to prevent the re-aggregation of the stripped nanosheets, and then stir with a high-speed mixer Five minutes, due to the adsorption of kaolin nanosheets, the pH of the solution will decrease after a period of time, so it is necessary to readjust the pH>9 afterwards, and then stir for five minutes with a high-speed mixer to obtain a dispersion of kaolin nanosheets;

步骤三:将步骤二中的得到的高岭土纳米片分散液与阳离子聚丙烯酰胺,通过层层堆叠的方法将高岭土纳米片负载到醋酸纤维素微滤膜表面。Step 3: The kaolin nanosheet dispersion obtained in step 2 and cationic polyacrylamide are used to load the kaolin nanosheets on the surface of the cellulose acetate microfiltration membrane by layer-by-layer stacking.

进一步的,高岭土40-50g与50-100ml的饱和的尿素溶液混合。Further, 40-50 g of kaolin is mixed with 50-100 ml of saturated urea solution.

进一步的,阳离子聚丙烯酰胺的分子量>700万,阳离子聚丙烯酰胺的溶度为0.1-10mg/L。Further, the molecular weight of the cationic polyacrylamide is >7 million, and the solubility of the cationic polyacrylamide is 0.1-10 mg/L.

进一步的,PH调节剂为NaOH或KOH中的一种或两种。Further, the pH regulator is one or both of NaOH or KOH.

进一步的,步骤三中高岭土纳米片的负载层数为1-300层。Further, the number of loaded layers of kaolin nanosheets in step 3 is 1-300 layers.

进一步的,步骤一中高岭土纳米片为单层高岭土纳米片或多层高岭土纳米片。Further, the kaolin nanosheets in step 1 are single-layer kaolin nanosheets or multilayer kaolin nanosheets.

进一步的,步骤一中HCl的浓度为1M,超声8-15min。Further, in the first step, the concentration of HCl is 1M, and the ultrasound is 8-15min.

进一步的,步骤三中醋酸纤维素微滤膜的孔径为0.45um。Further, the pore size of the cellulose acetate microfiltration membrane in step three is 0.45um.

阳离子聚丙烯酰胺购自:天津市光复精细化工研究所。Cationic polyacrylamide was purchased from: Tianjin Guangfu Fine Chemical Research Institute.

相对于现有技术,本发明所述的大通量超滤膜的制备方法具有以下优势:Compared with the prior art, the preparation method of the large flux ultrafiltration membrane of the present invention has the following advantages:

本发明所述的大通量超滤膜的制备方法,制备的高岭土超滤膜其初始通量是聚偏二氟乙烯超滤膜初始通量的十倍,并且还可以大大降低膜通量的衰减,减少膜污染,提高膜的使用寿命,提高水处理效率;阳离子聚丙烯酰胺交联剂通过静电作用增强高岭土纳米片间的结合力,提高了高岭土超滤膜在水中的稳定性,本发明方法简单易操作且易于规模化使用,利于推广。According to the preparation method of the large-flux ultrafiltration membrane of the present invention, the initial flux of the prepared kaolin ultrafiltration membrane is ten times that of the polyvinylidene fluoride ultrafiltration membrane, and can also greatly reduce the membrane flux. attenuation, reduce membrane fouling, increase the service life of the membrane, and improve water treatment efficiency; the cationic polyacrylamide crosslinking agent enhances the binding force between kaolin nanosheets through electrostatic interaction, and improves the stability of kaolin ultrafiltration membrane in water. The present invention The method is simple, easy to operate, and easy to use on a large scale, which is conducive to popularization.

附图说明Description of drawings

图1:在0.45um的醋酸纤维微滤膜表面以阳离子聚丙烯酰胺为交联剂,用层层堆叠方法负载50层高岭土纳米片的扫描电子显微镜图;Figure 1: Scanning electron microscope image of 50 layers of kaolin nanosheets loaded on the surface of 0.45um cellulose acetate microfiltration membrane with cationic polyacrylamide as crosslinking agent by layer stacking method;

图2:负载10层高岭土纳米片的高岭土超滤膜的BET图。Figure 2: BET diagram of the kaolin ultrafiltration membrane loaded with 10 layers of kaolin nanosheets.

图3:商业聚偏二氟乙烯超滤膜的BET图。Figure 3: BET plot of commercial polyvinylidene fluoride ultrafiltration membranes.

图4:用负载了10层的高岭土纳米片的高岭土超滤膜和商业聚偏二氟乙烯超滤膜过滤300mL BIT lake、300mL ZGC river、300mL 10mg/L的BSA(牛血清蛋白)、300mL 10mg/LHA(腐植酸)、300mL 10mg/L SA(海藻酸钠)溶液来获得过滤有机物溶液时膜的初始通量图;Figure 4: Using a kaolin ultrafiltration membrane loaded with 10 layers of kaolin nanosheets and a commercial polyvinylidene fluoride ultrafiltration membrane to filter 300mL BIT lake, 300mL ZGC river, 300mL 10mg/L BSA (bovine serum albumin), 300mL 10mg /LHA (humic acid), 300mL 10mg/L SA (sodium alginate) solution to obtain the initial flux figure of the membrane when filtering the organic solution;

图5:加入CPAM和Al3+后高岭土纳米片的zeta电势图;Figure 5: Zeta potential map of kaolin nanosheets after adding CPAM and Al 3+ ;

图6:加入CPAM和Al3+后高岭土纳米片的光度色散分析(PDA)图;Figure 6: Photometric dispersion analysis (PDA) diagram of kaolin nanosheets after adding CPAM and Al 3+ ;

图7:用负载了10层的高岭土纳米片的高岭土超滤膜过滤300mL BIT lake、300mLZGC river、300mL 10mg/L的BSA(牛血清蛋白)、300mL 10mg/L HA(腐植酸)、300mL 10mg/LSA(海藻酸钠)溶液来获得过滤有机物溶液时膜的相对通量图;Figure 7: 300mL BIT lake, 300mL ZGC river, 300mL 10mg/L BSA (bovine serum albumin), 300mL 10mg/L HA (humic acid), 300mL 10mg/L were filtered with a kaolin ultrafiltration membrane loaded with 10 layers of kaolin nanosheets. LSA (sodium alginate) solution to obtain the relative flux diagram of the membrane when filtering the organic solution;

图8:商业聚偏二氟乙烯超滤膜过滤300mL BIT lake、300mL ZGC river、300mL10mg/L的BSA(牛血清蛋白)、300mL 10mg/L HA(腐植酸)、300mL 10mg/L SA(海藻酸钠)溶液来获得过滤有机物溶液时膜的相对通量图。Figure 8: Commercial polyvinylidene fluoride ultrafiltration membrane filtration 300mL BIT lake, 300mL ZGC river, 300mL 10mg/L BSA (bovine serum albumin), 300mL 10mg/L HA (humic acid), 300mL 10mg/L SA (alginic acid Sodium) solution to obtain the relative flux diagram of the membrane when filtering the organic solution.

具体实施方式Detailed ways

除有定义外,以下实施例中所用的技术术语具有与本发明所属领域技术人员普遍理解的相同含义。以下实施例中所用的试验试剂,如无特殊说明,均为常规生化试剂;所述实验方法,如无特殊说明,均为常规方法。Unless otherwise defined, the technical terms used in the following embodiments have the same meaning as commonly understood by those skilled in the art to which the present invention belongs. The test reagents used in the following examples, unless otherwise specified, are conventional biochemical reagents; the experimental methods, unless otherwise specified, are conventional methods.

下面结合实施例及附图来详细说明本发明。The present invention will be described in detail below in conjunction with the embodiments and accompanying drawings.

将50g高岭土在80ml饱和的尿素溶液中在65℃下用分散机在200r的转速下搅拌80h,之后将烘干得到的插层复合物加入到浓度为1M的HCl中在60℃下超声十分钟,得到高岭土纳米片溶液,之后将高岭土纳米片溶液用NaOH调节至PH>9,再用高速搅拌机进行搅拌五分钟,之后再重新调节PH>9再用高速搅拌机进行搅拌五分钟来获取高岭土纳米片分散液。Stir 50g of kaolin in 80ml of saturated urea solution at 65°C with a disperser at a speed of 200r for 80h, then add the dried intercalation complex into 1M HCl and ultrasonicate at 60°C for ten minutes , to obtain a kaolin nanosheet solution, then adjust the kaolin nanosheet solution to pH>9 with NaOH, then stir for five minutes with a high-speed mixer, then readjust the pH>9 and then stir for five minutes with a high-speed mixer to obtain kaolin nanosheets Dispersions.

之后取出高岭土溶液将其稀释到浓度为50mg/L作为储备液。取出两份50ml的储备液一份加入CPAM,一份加入Al3+并用光度分散仪进行测试并记录絮凝指数值(FI值)。Afterwards, the kaolin solution was taken out and diluted to a concentration of 50 mg/L as a stock solution. Two parts of 50ml stock solution were taken out, one was added to CPAM, the other was added to Al 3+ and tested with a photometric disperser and recorded the flocculation index value (FI value).

再取出两份50ml的储备液一份加入CPAM,一份加入Al3+并用zeta电位及粒度分析仪进行测试并记录zeta电势值。Then take out two 50ml stock solutions, add one to CPAM, and one to add Al 3+ to test with zeta potential and particle size analyzer and record the zeta potential value.

如图5和图6所示,图5表明当zeta电势等于零时需要的Al3+的量将近是CPAM的100倍;图6表明当加入相同量的CPAM和Al3+时,加入CPAM后的FI值要更大。通过图5和图6可知CPAM对高岭土纳米片的胶粘性更好更适合做胶粘剂。As shown in Figure 5 and Figure 6, Figure 5 shows that when the zeta potential is equal to zero, the amount of Al 3+ required is nearly 100 times that of CPAM; Figure 6 shows that when the same amount of CPAM and Al 3+ is added, the The FI value is larger. It can be seen from Figure 5 and Figure 6 that CPAM has better adhesion to kaolin nanosheets and is more suitable for adhesives.

将1mL 100ppm分子量为800万-1500万的的阳离子聚丙烯酰胺(CPAM)滴到醋酸纤维素微滤膜上摇晃60s后倒出再用5mL的超纯水洗两次,之后加入2mL 0.3g/L的高岭土在0.1MPa条件下进行压滤,后用5mL的超纯水洗三次,此时在醋酸纤维素微滤膜上就负载了一层高岭土,如此下去负载10层,后用200mL超纯水冲洗膜。Drop 1mL of 100ppm cationic polyacrylamide (CPAM) with a molecular weight of 8 million to 15 million onto a cellulose acetate microfiltration membrane, shake for 60s, pour it out and wash it twice with 5mL of ultrapure water, then add 2mL of 0.3g/L The kaolin was filtered under the condition of 0.1MPa, and then washed three times with 5mL of ultrapure water. At this time, a layer of kaolin was loaded on the cellulose acetate microfiltration membrane, and then loaded for 10 layers, and finally washed with 200mL of ultrapure water. membrane.

用负载了10层的高岭土纳米片的高岭土超滤膜和商业聚偏二氟乙烯超滤膜过滤300mL BIT lake、300mL ZGC river、300mL 10mg/L的BSA(牛血清蛋白)、300mL 10mg/L HA(腐植酸)、300mL 10mg/L SA(海藻酸钠)溶液,同时用电子天平连接数据显示器采集数据,从而来获得过滤有机溶液时膜的初始通量图。Filter 300mL BIT lake, 300mL ZGC river, 300mL 10mg/L BSA (bovine serum albumin), 300mL 10mg/L HA with kaolin ultrafiltration membrane loaded with 10 layers of kaolin nanosheets and commercial polyvinylidene fluoride ultrafiltration membrane (humic acid), 300mL 10mg/L SA (sodium alginate) solution, and at the same time, use an electronic balance to connect to the data display to collect data, so as to obtain the initial flux diagram of the membrane when filtering the organic solution.

如图4所示,制备的高岭土超滤膜其初始通量大约是聚偏二氟乙烯超滤膜初始通量的十倍。As shown in Figure 4, the initial flux of the prepared kaolin ultrafiltration membrane is about ten times that of the polyvinylidene fluoride ultrafiltration membrane.

用负载了10层的高岭土纳米片的高岭土超滤膜和商业聚偏二氟乙烯超滤膜过滤300mL BIT lake、300mL ZGC river、300mL 10mg/L的BSA(牛血清蛋白)、300mL 10mg/L HA(腐植酸)、300mL 10mg/L SA(海藻酸钠)溶液,同时用电子天平连接数据显示器采集数据,从而来获得过滤有机溶液时膜的相对通量图。Filter 300mL BIT lake, 300mL ZGC river, 300mL 10mg/L BSA (bovine serum albumin), 300mL 10mg/L HA with kaolin ultrafiltration membrane loaded with 10 layers of kaolin nanosheets and commercial polyvinylidene fluoride ultrafiltration membrane (humic acid), 300mL 10mg/L SA (sodium alginate) solution, and at the same time, use an electronic balance to connect to the data display to collect data, so as to obtain the relative flux diagram of the membrane when filtering the organic solution.

如图7和图8所示,制备的高岭土超滤膜在过滤300mL溶液后其相对通量降低的程度要小于商业聚偏二氟乙烯超滤膜。As shown in Figures 7 and 8, the relative flux of the prepared kaolin ultrafiltration membrane was lower than that of the commercial polyvinylidene fluoride ultrafiltration membrane after filtering 300 mL of solution.

初始通量是表征:膜的处理效率即膜在单位时间内可以处理废水的量。The initial flux is a characterization: the treatment efficiency of the membrane is the amount of wastewater that the membrane can treat in unit time.

相对通量是表征:膜的抗污染能力这是因为在废水处理中膜的孔道会被废水中的污染物堵住造成膜的污染从而导致相对通量的下降。The relative flux is a characterization: the anti-fouling ability of the membrane. This is because the pores of the membrane will be blocked by pollutants in the wastewater in wastewater treatment, causing membrane fouling and resulting in a decrease in the relative flux.

相对通量下降的越快(即曲线越陡)就表明膜的抗污染能力越差。The faster the relative flux decreases (ie, the steeper the curve), the worse the anti-fouling ability of the membrane.

同时用电子天平连接数据显示器采集数据,从而来获得过滤有机溶液时膜的相对通量图。如图7和图8所示:制备的高岭土超滤膜在过滤300mL溶液后其相对通量降低的程度要小于商业聚偏二氟乙烯超滤膜。At the same time, the electronic balance is connected to the data display to collect data, so as to obtain the relative flux diagram of the membrane when filtering the organic solution. As shown in Figure 7 and Figure 8: the relative flux of the prepared kaolin ultrafiltration membrane after filtering 300mL solution is less than that of the commercial polyvinylidene fluoride ultrafiltration membrane.

以上所述仅为本发明的较佳实施例而已,并不用以限制本发明,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present invention shall be included in the scope of the present invention. within the scope of protection.

Claims (9)

1.一种大通量超滤膜的制备方法,其特征在于:包括如下步骤:1. a preparation method of large flux ultrafiltration membrane, is characterized in that: comprise the steps: 步骤一:高岭土与饱和的尿素溶液充分搅拌,烘干得到插层复合物,插层复合物加入到HCl溶液中进行超声,得到高岭土纳米片溶液;Step 1: kaolin and saturated urea solution are fully stirred, dried to obtain an intercalation compound, and the intercalation compound is added to HCl solution for ultrasonication to obtain a kaolin nanosheet solution; 步骤二:高岭土纳米片溶液用PH调节剂调节至PH>9,获得高岭土纳米片分散液;Step 2: the kaolin nanosheet solution is adjusted to pH>9 with a pH regulator to obtain a kaolin nanosheet dispersion; 步骤三:将步骤二中的得到的高岭土纳米片分散液与阳离子聚丙烯酰胺,通过层层堆叠的方法将高岭土纳米片负载到醋酸纤维素微滤膜表面。Step 3: The kaolin nanosheet dispersion obtained in step 2 and cationic polyacrylamide are used to load the kaolin nanosheets on the surface of the cellulose acetate microfiltration membrane by layer-by-layer stacking. 2.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:高岭土40-50g与50-100ml的饱和的尿素溶液混合。2. The preparation method of the large flux ultrafiltration membrane according to claim 1, characterized in that: 40-50 g of kaolin is mixed with the saturated urea solution of 50-100 ml. 3.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:阳离子聚丙烯酰胺的分子量>700万,阳离子聚丙烯酰胺的溶度为0.1-10mg/L。3. The preparation method of the large flux ultrafiltration membrane according to claim 1, characterized in that: the molecular weight of the cationic polyacrylamide is >7 million, and the solubility of the cationic polyacrylamide is 0.1-10 mg/L. 4.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:PH调节剂为NaOH或KOH中的一种或两种。4. The preparation method of large flux ultrafiltration membrane according to claim 1, characterized in that: the pH regulator is one or both of NaOH or KOH. 5.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:步骤三中高岭土纳米片的负载层数为1-300层。5. The preparation method of the large-flux ultrafiltration membrane according to claim 1, characterized in that: the number of loaded layers of kaolin nanosheets in step 3 is 1-300 layers. 6.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:步骤一中高岭土纳米片为单层高岭土纳米片或多层高岭土纳米片。6 . The method for preparing a large flux ultrafiltration membrane according to claim 1 , wherein the kaolin nanosheets in step 1 are single-layer kaolin nanosheets or multilayer kaolin nanosheets. 7.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:步骤一中高岭土与饱和的尿素溶液在55-70℃下用分散机在200r的转速下搅拌70-80h。7. The preparation method of the large-flux ultrafiltration membrane according to claim 1, characterized in that: kaolin and saturated urea solution are stirred at 55-70°C for 70-80h with a disperser at a rotating speed of 200r in step 1 . 8.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:步骤一中HCl的浓度为1M,超声8-15min。8. The preparation method of the large-flux ultrafiltration membrane according to claim 1, characterized in that: in step 1, the concentration of HCl is 1M, and the ultrasound is 8-15min. 9.根据权利要求1所述的大通量超滤膜的制备方法,其特征在于:步骤三中醋酸纤维素微滤膜的孔径为0.45um。9. The preparation method of the large flux ultrafiltration membrane according to claim 1, characterized in that: the pore size of the cellulose acetate microfiltration membrane in step 3 is 0.45um.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114832636A (en) * 2022-05-03 2022-08-02 北京工业大学 Preparation method of low-cost and large-area clay-based separation membrane for water treatment
CN115584171A (en) * 2022-10-12 2023-01-10 福建省荔松新型材料有限公司 High-weather-resistance coil steel coating and preparation method thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101734677A (en) * 2008-11-05 2010-06-16 北京化工大学 Method for stripping laminated inorganic material
WO2014004479A2 (en) * 2012-06-25 2014-01-03 Massachusetts Institute Of Technology Porous film
WO2018044298A1 (en) * 2016-08-31 2018-03-08 South Dakota Board Of Regents Multilayer thin film nanocomposite membranes prepared by molecular layer-by-layer assembly

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101734677A (en) * 2008-11-05 2010-06-16 北京化工大学 Method for stripping laminated inorganic material
WO2014004479A2 (en) * 2012-06-25 2014-01-03 Massachusetts Institute Of Technology Porous film
WO2018044298A1 (en) * 2016-08-31 2018-03-08 South Dakota Board Of Regents Multilayer thin film nanocomposite membranes prepared by molecular layer-by-layer assembly

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
HONG, JS ET AL.: "Role of clays in fouling-resistant clay-embedded polyelectrolyte multilayer membranes for wastewater effluent treatment", 《SEPARATION SCIENCE AND TECHNOLOGY》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114832636A (en) * 2022-05-03 2022-08-02 北京工业大学 Preparation method of low-cost and large-area clay-based separation membrane for water treatment
CN115584171A (en) * 2022-10-12 2023-01-10 福建省荔松新型材料有限公司 High-weather-resistance coil steel coating and preparation method thereof
CN115584171B (en) * 2022-10-12 2023-07-11 福建省荔松新型材料有限公司 High-weather-resistance coil steel coating and preparation method thereof

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Application publication date: 20181204