CN114984779A - Preparation method of high-flux cellulose forward osmosis membrane - Google Patents
Preparation method of high-flux cellulose forward osmosis membrane Download PDFInfo
- Publication number
- CN114984779A CN114984779A CN202210721144.0A CN202210721144A CN114984779A CN 114984779 A CN114984779 A CN 114984779A CN 202210721144 A CN202210721144 A CN 202210721144A CN 114984779 A CN114984779 A CN 114984779A
- Authority
- CN
- China
- Prior art keywords
- cellulose
- forward osmosis
- osmosis membrane
- cellulase
- membrane
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 229920002678 cellulose Polymers 0.000 title claims abstract description 107
- 239000001913 cellulose Substances 0.000 title claims abstract description 107
- 239000012528 membrane Substances 0.000 title claims abstract description 85
- 238000009292 forward osmosis Methods 0.000 title claims abstract description 52
- 238000002360 preparation method Methods 0.000 title claims abstract description 14
- 108010059892 Cellulase Proteins 0.000 claims abstract description 44
- 229940106157 cellulase Drugs 0.000 claims abstract description 44
- 229920000875 Dissolving pulp Polymers 0.000 claims abstract description 11
- 239000011148 porous material Substances 0.000 claims abstract description 11
- 238000000614 phase inversion technique Methods 0.000 claims abstract description 7
- 238000005530 etching Methods 0.000 claims abstract description 4
- 238000000034 method Methods 0.000 claims description 17
- 238000000576 coating method Methods 0.000 claims description 14
- 239000011248 coating agent Substances 0.000 claims description 13
- 238000005507 spraying Methods 0.000 claims description 5
- 238000004528 spin coating Methods 0.000 claims description 4
- 238000004519 manufacturing process Methods 0.000 claims description 3
- 239000013505 freshwater Substances 0.000 claims 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 21
- 238000000926 separation method Methods 0.000 abstract description 9
- 238000010612 desalination reaction Methods 0.000 abstract description 7
- 230000004907 flux Effects 0.000 abstract description 6
- 239000013535 sea water Substances 0.000 abstract description 4
- 239000002904 solvent Substances 0.000 abstract description 2
- 239000000835 fiber Substances 0.000 abstract 1
- 150000003839 salts Chemical class 0.000 abstract 1
- 239000010408 film Substances 0.000 description 17
- 239000000243 solution Substances 0.000 description 15
- 238000005516 engineering process Methods 0.000 description 12
- LFTLOKWAGJYHHR-UHFFFAOYSA-N N-methylmorpholine N-oxide Chemical compound CN1(=O)CCOCC1 LFTLOKWAGJYHHR-UHFFFAOYSA-N 0.000 description 8
- 238000006116 polymerization reaction Methods 0.000 description 7
- IVNPXOUPZCTJAK-UHFFFAOYSA-N 4-methylmorpholin-4-ium;hydroxide Chemical compound O.CN1CCOCC1 IVNPXOUPZCTJAK-UHFFFAOYSA-N 0.000 description 6
- 238000005191 phase separation Methods 0.000 description 6
- -1 salt ions Chemical class 0.000 description 6
- 239000003153 chemical reaction reagent Substances 0.000 description 5
- 239000000463 material Substances 0.000 description 5
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 4
- 238000001914 filtration Methods 0.000 description 4
- 239000002131 composite material Substances 0.000 description 3
- 238000001000 micrograph Methods 0.000 description 3
- 238000000108 ultra-filtration Methods 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 230000003373 anti-fouling effect Effects 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 239000012267 brine Substances 0.000 description 2
- 125000002091 cationic group Chemical group 0.000 description 2
- 238000001223 reverse osmosis Methods 0.000 description 2
- 239000012266 salt solution Substances 0.000 description 2
- 239000011780 sodium chloride Substances 0.000 description 2
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 description 2
- 239000010409 thin film Substances 0.000 description 2
- XOJVVFBFDXDTEG-UHFFFAOYSA-N Norphytane Natural products CC(C)CCCC(C)CCCC(C)CCCC(C)C XOJVVFBFDXDTEG-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 125000003118 aryl group Chemical group 0.000 description 1
- 238000010560 atom transfer radical polymerization reaction Methods 0.000 description 1
- 238000006065 biodegradation reaction Methods 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000002041 carbon nanotube Substances 0.000 description 1
- 229910021393 carbon nanotube Inorganic materials 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 229910021389 graphene Inorganic materials 0.000 description 1
- 150000004820 halides Chemical class 0.000 description 1
- 239000012510 hollow fiber Substances 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 239000003999 initiator Substances 0.000 description 1
- 239000003446 ligand Substances 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000012621 metal-organic framework Substances 0.000 description 1
- 239000000178 monomer Substances 0.000 description 1
- 239000002086 nanomaterial Substances 0.000 description 1
- 239000002071 nanotube Substances 0.000 description 1
- 229920002492 poly(sulfone) Polymers 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- GROMGGTZECPEKN-UHFFFAOYSA-N sodium metatitanate Chemical compound [Na+].[Na+].[O-][Ti](=O)O[Ti](=O)O[Ti]([O-])=O GROMGGTZECPEKN-UHFFFAOYSA-N 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 229920001059 synthetic polymer Polymers 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 238000000844 transformation Methods 0.000 description 1
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D71/00—Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
- B01D71/06—Organic material
- B01D71/08—Polysaccharides
- B01D71/10—Cellulose; Modified cellulose
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D67/00—Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
- B01D67/0002—Organic membrane manufacture
- B01D67/0009—Organic membrane manufacture by phase separation, sol-gel transition, evaporation or solvent quenching
- B01D67/0013—Casting processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D67/00—Processes specially adapted for manufacturing semi-permeable membranes for separation processes or apparatus
- B01D67/0081—After-treatment of organic or inorganic membranes
- B01D67/0093—Chemical modification
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D69/00—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
- B01D69/02—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor characterised by their properties
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/445—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by forward osmosis
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2323/00—Details relating to membrane preparation
- B01D2323/26—Spraying processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2325/00—Details relating to properties of membranes
- B01D2325/02—Details relating to pores or porosity of the membranes
- B01D2325/022—Asymmetric membranes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/08—Seawater, e.g. for desalination
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
- Y02A20/131—Reverse-osmosis
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Engineering & Computer Science (AREA)
- Manufacturing & Machinery (AREA)
- Dispersion Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
本发明公开一种高通量纤维素正渗透膜的制备方法,涉及膜分离和海水淡化技术领域。本发明的制备方法包括以下步骤:1)将纤维素溶解在溶剂中,采用相转化法制备纤维素膜;2)利用纤维素酶对纤维素膜进行单面蚀刻处理获得具有非对称结构的纤维素正渗透膜。本研究发明的纤维素正渗透膜具有不对称的孔结构,呈现优异的水通量和盐截留率,且制备工艺简单,环境友好,可大规模生产。
The invention discloses a preparation method of a high-flux cellulose forward osmosis membrane, and relates to the technical field of membrane separation and seawater desalination. The preparation method of the present invention includes the following steps: 1) dissolving cellulose in a solvent, and preparing a cellulose film by a phase inversion method; 2) using cellulase to perform single-sided etching treatment on the cellulose film to obtain fibers with an asymmetric structure Prime forward osmosis membrane. The cellulose forward osmosis membrane invented in this study has an asymmetric pore structure, exhibits excellent water flux and salt rejection, and has a simple preparation process that is environmentally friendly and can be mass-produced.
Description
技术领域technical field
本发明公开一种-高通量纤维素正渗透膜的制备方法,涉及膜分离和海水淡化技术领域。The invention discloses a preparation method of a high-flux cellulose forward osmosis membrane, which relates to the technical field of membrane separation and seawater desalination.
背景技术Background technique
目前,清洁水的严重短缺正在挑战我们的生存和进一步发展。膜激发的脱盐策略由于其简单操作和高分离效率,已被广泛认为是获取清洁水的有效的方法之一。膜诱导的水分离技术可以通过外部压力差或内部化学势差进行,这分别形成了反渗透(RO)和正渗透(FO)方法。与反渗透工艺相比,正渗透具有能源需求低、抗污能力强等优点。Currently, a severe shortage of clean water is challenging our existence and further development. Membrane-inspired desalination strategies have been widely recognized as one of the effective methods to obtain clean water due to their simple operation and high separation efficiency. Membrane-induced water separation techniques can be carried out by external pressure differences or internal chemical potential differences, which form the reverse osmosis (RO) and forward osmosis (FO) methods, respectively. Compared with the reverse osmosis process, forward osmosis has the advantages of low energy demand and strong anti-fouling ability.
膜材料是影响FO方法性能的关键因素。根据文献报道,目前的FO膜通常具有双层结构(即薄膜复合材料,TFC),由多孔支撑层和致密活性层组成,其中支撑层提供强度,活性层实现分离行为。这种FO膜通常是在聚砜的支撑层材料上原位生长芳香族聚合物(作为活性层)。尽管技术已经成熟,但基于合成聚合物的薄膜复合膜仍然存在低亲水性、弱抗污能力和难以生物降解等缺点。因此,一些纳米材料,例如钛酸钠纳米管、碳纳米管、氧化石墨烯和金属有机框架等被引入到上述FO膜中,以加强其亲水性和脱盐效率,然而,这种行为增加了FO膜的制造成本并使制造过程复杂化。Membrane material is a key factor affecting the performance of the FO method. According to literature reports, current FO membranes usually have a bilayer structure (i.e., thin film composites, TFCs), consisting of a porous support layer and a dense active layer, where the support layer provides strength and the active layer realizes the separation behavior. Such FO membranes are typically in situ grown aromatic polymers (as the active layer) on a polysulfone support layer material. Although the technology has matured, thin-film composite membranes based on synthetic polymers still suffer from low hydrophilicity, weak antifouling ability, and difficult biodegradation. Therefore, some nanomaterials, such as sodium titanate nanotubes, carbon nanotubes, graphene oxide, and metal organic frameworks, etc., were introduced into the above-mentioned FO membranes to enhance their hydrophilicity and desalination efficiency, however, this behavior increased the The manufacturing cost of FO membranes and complicates the manufacturing process.
由于优良的亲水性、生物相容性和相对低廉的成本,天然纤维素被用来构建分离膜。中国专利CN106237875A公开了一种纤维素基阳离子选择性过滤膜的制备方法及其产品。该方法利用均相溶解试剂或非均相试剂将纤维素溶解或分散在溶剂中制备出多孔纤维素薄膜,然后用酰卤试剂与多孔纤维素薄膜反应,得到表面改性的纤维素基大分子引发剂,然后再将制得的纤维素基大分子引发剂在催化剂和配体作用下,与阳离子单体进行原子转移自由基聚合,得到纤维素基阳离子选择性过滤膜。中国专利CN101007240A公开了一种纤维素中空纤维超滤膜的制备方法,利用沉浸相转化法和干湿法得到纤维素中空膜,该膜为指状孔支撑层非对称结构,具有良好的水处理应用前景。中国专利CN103877867A公开了一种纤维素超滤膜制备方法,是在低温条件下获得了由支撑层和纳米孔纤维素皮层组成的纤维素超滤复合膜。以上专利都是利用纤维素材料制备纤维素分离膜,但其制备过程都相对复杂,可操作性差,且膜的水通量都较低,因此,有必要开发一种简单的方法制备出高通量的纤维素分离膜。在这项研究中,我们通过简单的纤维素酶蚀刻策略,从绿色纤维素材料中开发了一种低成本但超高水通量的纤维素正渗透膜。我们将纤维素酶涂覆在纤维素膜的单侧表面,使之与纤维素反应。这种行为引发了纤维素膜独特的不对称孔结构,包括疏松层和致密层。其中多孔的疏松层支持高通量的水传输,而致密结构则有利于截留系统中的盐离子。Natural cellulose is used to construct separation membranes due to its excellent hydrophilicity, biocompatibility, and relatively low cost. Chinese patent CN106237875A discloses a preparation method and products of a cellulose-based cation selective filtration membrane. The method utilizes a homogeneous dissolving reagent or a heterogeneous reagent to dissolve or disperse cellulose in a solvent to prepare a porous cellulose film, and then use an acid halide reagent to react with the porous cellulose film to obtain surface-modified cellulose-based macromolecules The cellulose-based macromolecular initiator is then subjected to atom transfer radical polymerization with cationic monomers under the action of catalysts and ligands to obtain a cellulose-based cationic selective filtration membrane. Chinese patent CN101007240A discloses a preparation method of cellulose hollow fiber ultrafiltration membrane. The cellulose hollow membrane is obtained by the immersion phase inversion method and the dry-wet method. application prospects. Chinese patent CN103877867A discloses a method for preparing a cellulose ultrafiltration membrane, which is to obtain a cellulose ultrafiltration composite membrane composed of a support layer and a nanoporous cellulose skin layer under low temperature conditions. The above patents all use cellulose materials to prepare cellulose separation membranes, but the preparation process is relatively complex, the operability is poor, and the water flux of the membrane is low. Therefore, it is necessary to develop a simple method to prepare high-pass amount of cellulose separation membrane. In this study, we developed a low-cost yet ultra-high water flux cellulose forward osmosis membrane from green cellulose materials through a simple cellulase etching strategy. We coat the cellulase on one side of the cellulose membrane to react with cellulose. This behavior triggers the unique asymmetric pore structure of cellulose membranes, including loose and dense layers. The porous layer supports high-flux water transport, while the dense structure is conducive to trapping salt ions in the system.
发明内容SUMMARY OF THE INVENTION
本发明针对以上现有的问题,提供了一种高通量纤维素正渗透膜的制备方法。In view of the above existing problems, the present invention provides a preparation method of a high-flux cellulose forward osmosis membrane.
为实现上述目的,本发明的技术方案为:For achieving the above object, the technical scheme of the present invention is:
一种高通量纤维素正渗透膜的制备方法,包括以下步骤:A preparation method of a high-flux cellulose forward osmosis membrane, comprising the following steps:
1)取溶解浆溶解于N-甲基吗啉-N-氧化物 (NMMO) 的水溶液中,通过相转化法得到纤维素膜。1) Dissolve the dissolving pulp in an aqueous solution of N-methylmorpholine-N-oxide (NMMO), and obtain a cellulose film by a phase inversion method.
2)在纤维素膜单面涂覆纤维素酶溶液,然后放入恒温培养箱中处理,即可得到具有非对称孔道结构的纤维素正渗透膜。2) Coating the cellulase solution on one side of the cellulose membrane, and then placing it in a constant temperature incubator for processing, the cellulose forward osmosis membrane with asymmetric pore structure can be obtained.
进一步地,步骤1)中溶解浆的纤维素含量高于90 %。Further, the cellulose content of the dissolving pulp in step 1) is higher than 90%.
进一步地,步骤1)中溶解浆的聚合度为400 ~ 600。Further, the polymerization degree of dissolving pulp in step 1) is 400~600.
进一步地,步骤1)中相转化法以刮涂的方式成膜。Further, the phase inversion method in step 1) forms a film by means of blade coating.
进一步地,步骤2)中纤维素酶可涂覆在纤维素膜的上表面或者下表面。Further, in step 2), the cellulase can be coated on the upper surface or the lower surface of the cellulose film.
进一步地,步骤2)中纤维素酶的用量为0.1 ~ 2 ml/m2。Further, the consumption of cellulase in step 2) is 0.1~2 ml/m 2 .
进一步地,步骤2)中纤维素酶的涂覆方式包括喷涂、刮涂、旋涂等。Further, the coating method of the cellulase in step 2) includes spray coating, blade coating, spin coating and the like.
进一步地,步骤2)中恒温培养箱的处理条件为处理时间为1 min ~ 30 min。Further, the processing conditions of the constant temperature incubator in step 2) are that the processing time is 1 min to 30 min.
由上述制备方法制备的纤维素正渗透膜具有不对称孔结构,具有优异的海水淡化性能,且制备工艺简单,环境友好,可大规模生产。The cellulose forward osmosis membrane prepared by the above preparation method has an asymmetric pore structure, has excellent seawater desalination performance, has a simple preparation process, is environmentally friendly, and can be produced on a large scale.
本发明的有益之处是:The benefits of the present invention are:
(1)本发明提出了一种高通量纤维素正渗透膜的制备方法,具有操作简单,成本较低等特点。(1) The present invention proposes a method for preparing a high-flux cellulose forward osmosis membrane, which has the characteristics of simple operation and low cost.
(2)本发明制备的纤维素正渗透膜是通过纤维素酶单面刻蚀纤维素膜策略构建,具有绿色环保特性,是一种低碳策略。(2) The cellulose forward osmosis membrane prepared by the present invention is constructed through the strategy of cellulase single-sided etching of the cellulose membrane, has green environmental protection characteristics, and is a low-carbon strategy.
(3)本发明构建的纤维素正渗透膜具有非对称结构,包括致密层和多孔输送层,实现水的快速传输和盐离子的有效截留,可为高效海水淡化提供选择。(3) The cellulose forward osmosis membrane constructed by the present invention has an asymmetric structure, including a dense layer and a porous transport layer, which realizes the rapid transmission of water and the effective interception of salt ions, and provides options for efficient seawater desalination.
附图说明Description of drawings
图1是实施1中原始纤维素膜的场发射扫描电子显微镜图;Fig. 1 is the field emission scanning electron microscope image of the original cellulose film in
图2是实施1中纤维素正渗透膜的场发射扫描电子显微镜图;Fig. 2 is the field emission scanning electron microscope picture of cellulose forward osmosis membrane in
图3是实施1中原始纤维素膜和纤维素正渗透膜对1mol/L NaCl溶液的过滤性能对比图;Fig. 3 is the filtration performance comparison diagram of original cellulose membrane and cellulose forward osmosis membrane to 1mol/L NaCl solution in
图4是实施1中纤维素正渗透膜对不同盐溶液的过滤性能图;Fig. 4 is the filtration performance figure of cellulose forward osmosis membrane to different salt solutions in
图5是不同处理时间下纤维素正渗透膜的场发射扫描电子显微镜图;Fig. 5 is the field emission scanning electron microscope image of cellulose forward osmosis membrane under different treatment time;
图6是不同处理时间下纤维素正渗透膜的照片图;Fig. 6 is the photograph figure of cellulose forward osmosis membrane under different treatment time;
图7是纤维素酶处理时间对纤维素正渗透膜性能的影响。Figure 7 is the effect of cellulase treatment time on the performance of cellulose forward osmosis membrane.
具体实施方式Detailed ways
本发明提供一种-高通量纤维素正渗透膜的制备方法:The invention provides a preparation method of a high-flux cellulose forward osmosis membrane:
下面结合具体实施例对本发明作进一步说明,以使本领域的技术人员可以更好地理解本发明并能予以实施,但所举实施例不作为对本发明的限定。The present invention will be further described below with reference to specific embodiments, so that those skilled in the art can better understand the present invention and implement it, but the embodiments are not intended to limit the present invention.
实施例1Example 1
a. 取聚合度为400,纤维素含量为90 %的溶解浆溶解在NMMO/水溶液中,然后采用相分离技术刮涂制备原始纤维素膜。a. The dissolving pulp with a degree of polymerization of 400 and a cellulose content of 90 % was dissolved in NMMO/water solution, and then the original cellulose film was prepared by blade coating using phase separation technology.
b. 采用喷涂技术在纤维素膜上表面涂覆纤维素酶溶液,纤维素酶的用量为0.83ml/m2。b. The cellulase solution was coated on the surface of the cellulose film by spraying technology, and the dosage of cellulase was 0.83ml/m 2 .
c.在培养箱中进行纤维素酶处理,处理时间:30 min,处理温度:40 ℃,处理湿度:60 %。c. Carry out cellulase treatment in an incubator, treatment time: 30 min, treatment temperature: 40 °C, treatment humidity: 60 %.
通过以上步骤得到的纤维素正渗透膜,与原始纤维素膜(图1)相比,纤维素酶处理的纤维素正渗透膜呈现对堆成结构(图2),有助于水分子的传输和盐离子的截留。Compared with the original cellulose membrane (Figure 1), the cellulose forward osmosis membrane obtained by the above steps, the cellulose forward osmosis membrane treated with cellulase presents a stacked structure (Figure 2), which is conducive to the transport of water molecules and retention of salt ions.
实施例2Example 2
a. 取聚合度为500,纤维素含量为96 %的溶解浆溶解在NMMO/水溶液中,然后采用相分离技术刮涂制备原始纤维素膜。a. The dissolving pulp with a degree of polymerization of 500 and a cellulose content of 96 % was dissolved in NMMO/water solution, and then the original cellulose film was prepared by blade coating using phase separation technology.
b. 采用刮涂技术在纤维素膜上表面涂覆纤维素酶溶液,纤维素酶的用量为1.66ml/m2。b. The cellulase solution was coated on the surface of the cellulose film by the blade coating technique, and the dosage of cellulase was 1.66ml/m 2 .
c. 在恒温箱中进行纤维素酶处理,处理时间:10 min,处理温度:30 ℃,处理湿度:40 %。c. Carry out cellulase treatment in an incubator, treatment time: 10 min, treatment temperature: 30 °C, treatment humidity: 40 %.
通过以上步骤得到的纤维素正渗透膜,与原始纤维素膜相比,纤维素酶处理的纤维素正渗透膜表面呈现出多孔结构,有助于水分子的传输和盐离子的截留。Compared with the original cellulose membrane, the cellulose forward osmosis membrane obtained by the above steps has a porous structure on the surface of the cellulose forward osmosis membrane treated with cellulase, which is helpful for the transport of water molecules and the interception of salt ions.
实施例3Example 3
a. 取聚合度为600,纤维素含量为94 %的溶解浆溶解在NMMO/水溶液中,然后采用相分离技术刮涂制备原始纤维素膜。a. The dissolving pulp with a degree of polymerization of 600 and a cellulose content of 94 % was dissolved in NMMO/water solution, and then the original cellulose film was prepared by blade coating using phase separation technology.
b. 采用旋涂技术在纤维素膜上表面涂覆纤维素酶溶液,纤维素酶的用量为1.66ml/m2。b. Use spin coating technology to coat the cellulase solution on the surface of the cellulose membrane, and the dosage of cellulase is 1.66ml/m 2 .
c. 在恒温箱中进行纤维素酶处理,处理时间:10 min,处理温度:60 ℃,处理湿度:60 %。c. Carry out cellulase treatment in an incubator, treatment time: 10 min, treatment temperature: 60 ℃, treatment humidity: 60 %.
通过以上步骤得到的纤维素正渗透膜,与原始纤维素膜相比,纤维素酶处理的纤维素正渗透膜表面呈现多孔结构,有助于水分子的传输和盐离子的截留。Compared with the original cellulose membrane, the cellulose forward osmosis membrane obtained by the above steps has a porous structure on the surface of the cellulose forward osmosis membrane treated with cellulase, which is helpful for the transport of water molecules and the interception of salt ions.
实施例4Example 4
a. 取聚合度为400,纤维素含量为90 %的溶解浆溶解在NMMO/水溶液中,然后采用相分离技术刮涂制备原始纤维素膜。a. The dissolving pulp with a degree of polymerization of 400 and a cellulose content of 90 % was dissolved in NMMO/water solution, and then the original cellulose film was prepared by blade coating using phase separation technology.
b. 采用旋涂技术在纤维素膜上表面涂覆纤维素酶溶液,纤维素酶的用量为1.66ml/m2。b. Use spin coating technology to coat the cellulase solution on the surface of the cellulose membrane, and the dosage of cellulase is 1.66ml/m 2 .
c. 在恒温箱中进行纤维素酶处理,处理时间:30 min,处理温度:60 ℃,处理湿度:60 %。c. Carry out cellulase treatment in an incubator, treatment time: 30 min, treatment temperature: 60 ℃, treatment humidity: 60 %.
通过以上步骤得到的纤维素正渗透膜,与原始纤维素膜相比,纤维素酶的过度处理使得纤维素正渗透膜表面呈现出较多大孔。Compared with the original cellulose membrane, the cellulose forward osmosis membrane obtained by the above steps is over-treated with cellulase, so that the surface of the cellulose forward osmosis membrane presents more macropores.
实施例5Example 5
a. 取聚合度为500,纤维素含量为96 %的溶解浆溶解在NMMO/水溶液中,然后采用相分离技术刮涂制备原始纤维素膜。a. The dissolving pulp with a degree of polymerization of 500 and a cellulose content of 96 % was dissolved in NMMO/water solution, and then the original cellulose film was prepared by blade coating using phase separation technology.
b. 采用喷涂技术在纤维素膜上表面涂覆纤维素酶溶液,纤维素酶的用量为0.83ml/m2。b. The cellulase solution was coated on the surface of the cellulose film by spraying technology, and the dosage of cellulase was 0.83ml/m 2 .
c. 在恒温箱中进行纤维素酶处理,处理时间:30 min,处理温度:60 ℃,处理湿度:90 %。c. Carry out cellulase treatment in an incubator, treatment time: 30 min, treatment temperature: 60 °C, treatment humidity: 90 %.
通过以上步骤得到的纤维素正渗透膜,与原始纤维素膜相比,纤维素酶处理的纤维素正渗透膜表面呈现大小不一的孔隙结构。The cellulose forward osmosis membrane obtained by the above steps, compared with the original cellulose membrane, the surface of the cellulose forward osmosis membrane treated with cellulase presents pore structures of different sizes.
实施例6Example 6
a. 取聚合度为600,纤维素含量为94 %的溶解浆溶解在NMMO/水溶液中,然后采用相分离技术刮涂制备原始纤维素膜。a. The dissolving pulp with a degree of polymerization of 600 and a cellulose content of 94 % was dissolved in NMMO/water solution, and then the original cellulose film was prepared by blade coating using phase separation technology.
b. 采用喷涂技术在纤维素膜上表面涂覆纤维素酶溶液,纤维素酶的用量为0.83ml/m2。b. The cellulase solution was coated on the surface of the cellulose film by spraying technology, and the dosage of cellulase was 0.83ml/m 2 .
c. 在恒温箱中进行纤维素酶处理,处理时间:10 min,处理温度:30 ℃,处理湿度:40 %。c. Carry out cellulase treatment in an incubator, treatment time: 10 min, treatment temperature: 30 °C, treatment humidity: 40 %.
通过以上步骤得到的纤维素正渗透膜,与原始纤维素膜相比,纤维素酶处理的纤维素正渗透膜表面呈现出较小的孔隙结构。Compared with the original cellulose membrane, the cellulose forward osmosis membrane obtained by the above steps has a smaller pore structure on the surface of the cellulose forward osmosis membrane treated with cellulase.
图1和图2分别是实施1中原始纤维素膜和纤维素正渗透膜的场发射扫描电子显微镜图。相转化法赋予原始纤维素膜一种特殊的结构,其上、下表面致密,中部呈多孔状(图1)。实施1中纤维素酶处理使纤维素膜致密的表面发生破坏,显著提高了其孔径和孔隙率(图2)。FIG. 1 and FIG. 2 are field emission scanning electron microscope images of the original cellulose membrane and the cellulose forward osmosis membrane in Example 1, respectively. The phase inversion method endows the pristine cellulose membrane with a special structure with dense upper and lower surfaces and a porous center (Figure 1). The cellulase treatment in Example 1 disrupted the dense surface of the cellulose membrane and significantly increased its pore size and porosity (Figure 2).
本发明只是将纤维素酶涂覆在原始纤维素膜的上表面,破坏上表面的致密结构,但不影响下表面的致密结构。这样的行为最终引发纤维素材料的不对称孔结构。纤维素正渗透膜的多孔层能够有效运输水分子,其致密层可以排斥系统中盐离子,纤维素正渗透膜的水通量达到135.75 LMH,是原始纤维素膜的17倍(图3)。In the present invention, the cellulase is only coated on the upper surface of the original cellulose film, which destroys the dense structure of the upper surface, but does not affect the dense structure of the lower surface. Such behavior ultimately induces the asymmetric pore structure of the cellulosic material. The porous layer of the cellulose forward osmosis membrane can effectively transport water molecules, and its dense layer can repel salt ions in the system. The water flux of the cellulose forward osmosis membrane reaches 135.75 LMH, which is 17 times that of the original cellulose membrane (Figure 3).
在不同浓度的NaCl溶液体系中,纤维素正渗透膜也表现较高的水通量(大于120LMH)和较低的盐水比(低于0.53 g⋅L−1)。The cellulose forward osmosis membrane also exhibited higher water flux (greater than 120LMH) and lower brine ratio (below 0.53 g⋅L −1 ) in different concentrations of NaCl solution.
纤维素正渗透膜的脱盐性能良好,也适用于其他盐溶液的分离。例如,1 M Na2SO4和MgCl2体系,也表现出高水通量(167.75,174.25 LMH),同时,保持较低的盐水比(0.14 g⋅L−1,0.12 g⋅L−1)(图4)。The desalination performance of cellulose forward osmosis membrane is good, and it is also suitable for the separation of other salt solutions. For example, the 1 M Na 2 SO 4 and MgCl 2 systems also exhibited high water fluxes (167.75, 174.25 LMH), while maintaining low brine ratios (0.14 g⋅L −1 , 0.12 g⋅L −1 ) (Figure 4).
通过不同纤维素酶处理时间观察纤维素正渗透膜的形貌发现,随着纤维素酶处理时间的延长,纤维素正渗透膜表面的孔径逐渐增大(图5)。纤维素酶处理时间过长会引起纤维素正渗透膜的过度损伤 (图6),使纤维素正渗透膜结构破碎,降低其工作稳定性。By observing the morphology of the cellulose forward osmosis membrane with different cellulase treatment time, it was found that with the prolongation of the cellulase treatment time, the pore size of the surface of the cellulose forward osmosis membrane gradually increased (Fig. 5). Cellulase treatment for too long will cause excessive damage to the cellulose forward osmosis membrane (Fig. 6), break the structure of the cellulose forward osmosis membrane, and reduce its working stability.
纤维素酶处理时间的适当延长可以增强纤维素正渗透膜的渗透性能(图7)。Proper extension of cellulase treatment time can enhance the permeation performance of cellulose forward osmosis membranes (Fig. 7).
本发明使用的其他试剂均为现有技术可购买或配制的试剂,不再累述。Other reagents used in the present invention are all reagents that can be purchased or prepared in the prior art, and will not be described again.
以上所述实施例仅是为充分说明本发明而所举的较佳的实施例,本发明的保护范围不限于此。本技术领域的技术人员在本发明基础上所作的等同替代或变换,均在本发明的保护范围之内。本发明的保护范围以权利要求书为准。The above-mentioned embodiments are only preferred embodiments for fully illustrating the present invention, and the protection scope of the present invention is not limited thereto. Equivalent substitutions or transformations made by those skilled in the art on the basis of the present invention are all within the protection scope of the present invention. The protection scope of the present invention is subject to the claims.
Claims (6)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202210721144.0A CN114984779A (en) | 2022-06-24 | 2022-06-24 | Preparation method of high-flux cellulose forward osmosis membrane |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202210721144.0A CN114984779A (en) | 2022-06-24 | 2022-06-24 | Preparation method of high-flux cellulose forward osmosis membrane |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN114984779A true CN114984779A (en) | 2022-09-02 |
Family
ID=83037025
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202210721144.0A Pending CN114984779A (en) | 2022-06-24 | 2022-06-24 | Preparation method of high-flux cellulose forward osmosis membrane |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN114984779A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116688774A (en) * | 2023-04-07 | 2023-09-05 | 福建农林大学 | Forward osmosis membrane preparation method based on modified cellulose buffer layer and product thereof |
Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2001092382A1 (en) * | 2000-06-01 | 2001-12-06 | Ucb S.A. | Films and uses thereof |
| CN102228801A (en) * | 2011-05-16 | 2011-11-02 | 何涛 | Hydrophobically modified distillation membrane material of high throughout and high salt rejection rate and application thereof |
| CN103785301A (en) * | 2014-02-13 | 2014-05-14 | 中国科学院上海高等研究院 | Cellulose acetate forward osmosis film material and preparation method thereof |
| CN105597551A (en) * | 2015-10-16 | 2016-05-25 | 福建农林大学 | Production method of regenerated cellulose nanofiltration membrane |
| JP2016129220A (en) * | 2014-11-27 | 2016-07-14 | ユニバーシティ マラヤ | Manufacturing method of nanowire |
| CN107441960A (en) * | 2017-08-02 | 2017-12-08 | 同济大学 | The preparation method of high-performance Triafol T forward osmosis membrane |
| CN107855007A (en) * | 2017-07-13 | 2018-03-30 | 枫科(北京)膜技术有限公司 | A kind of asymmetric forward osmosis membrane and preparation method thereof |
| CN113084960A (en) * | 2021-04-26 | 2021-07-09 | 齐鲁工业大学 | Corn straw board and preparation method thereof |
| CN113201934A (en) * | 2021-04-27 | 2021-08-03 | 苏州大学 | Water-based super-hydrophobic coating and preparation method and application thereof |
-
2022
- 2022-06-24 CN CN202210721144.0A patent/CN114984779A/en active Pending
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2001092382A1 (en) * | 2000-06-01 | 2001-12-06 | Ucb S.A. | Films and uses thereof |
| CN102228801A (en) * | 2011-05-16 | 2011-11-02 | 何涛 | Hydrophobically modified distillation membrane material of high throughout and high salt rejection rate and application thereof |
| CN103785301A (en) * | 2014-02-13 | 2014-05-14 | 中国科学院上海高等研究院 | Cellulose acetate forward osmosis film material and preparation method thereof |
| JP2016129220A (en) * | 2014-11-27 | 2016-07-14 | ユニバーシティ マラヤ | Manufacturing method of nanowire |
| CN105597551A (en) * | 2015-10-16 | 2016-05-25 | 福建农林大学 | Production method of regenerated cellulose nanofiltration membrane |
| CN107855007A (en) * | 2017-07-13 | 2018-03-30 | 枫科(北京)膜技术有限公司 | A kind of asymmetric forward osmosis membrane and preparation method thereof |
| CN107441960A (en) * | 2017-08-02 | 2017-12-08 | 同济大学 | The preparation method of high-performance Triafol T forward osmosis membrane |
| CN113084960A (en) * | 2021-04-26 | 2021-07-09 | 齐鲁工业大学 | Corn straw board and preparation method thereof |
| CN113201934A (en) * | 2021-04-27 | 2021-08-03 | 苏州大学 | Water-based super-hydrophobic coating and preparation method and application thereof |
Non-Patent Citations (2)
| Title |
|---|
| YAN CHENG等: "A novel strategy for fabricating robust superhydrophobic fabrics by environmentally-friendly enzyme etching", CHEMICAL ENGINEERING JOURNAL, vol. 355, pages 291 * |
| YUAN HONGMEI等: "Engineered Janus cellulose membrane with the asymmetric-pore structure for the superhigh-water flux desalination", CARBOHYDRATE POLYMERS, vol. 291, no. 2022, pages 119601 * |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116688774A (en) * | 2023-04-07 | 2023-09-05 | 福建农林大学 | Forward osmosis membrane preparation method based on modified cellulose buffer layer and product thereof |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US10179314B2 (en) | Method for the high-throughput preparation of carbon nanotube hollow fiber membranes | |
| CN105396466B (en) | A kind of cellulose nanofiber-graphene oxide hybrid composite ultrafiltration membrane and preparation method thereof | |
| CN103223302B (en) | A preparation method of self-assembled covalently cross-linked nanofiltration membrane | |
| US11583808B2 (en) | Method of preparation of conductive polymer/carbon nanotube composite nanofiltration membrane and the use thereof | |
| CN111346523B (en) | Multifunctional bio-based composite microporous membrane and preparation method thereof | |
| KR101250310B1 (en) | Polyamide reverse osmosis membrane using polysulfone supporting material containing carbon nanotube and manufacturing method thereof | |
| CN110743400B (en) | Preparation method of copper ion-doped alginate hydrogel antibacterial filtering membrane | |
| CN103785301B (en) | A kind of Cellulose acetate forward osmotic membrane material and preparation method thereof | |
| CN105498547B (en) | A kind of preparation method of low pressure positive charge hollow fiber nanofiltration membrane | |
| CN109304088A (en) | A kind of seawater desalination membrane resistant to strong acid and alkali and its preparation method and application | |
| CN106268323A (en) | A kind of n-trimethyl chitosan chloride/polyacrylic acid composite nanometer filtering film and preparation method thereof | |
| CN106823865A (en) | A kind of aromatic polyamide composite reverse osmosis membrane and preparation method for being grafted carbon fluorine class material and aminoglycoside antibiotics | |
| CN108187511A (en) | High flux and high retention ratio polyamide composite reverse osmosis membrane and preparation method thereof | |
| CN113117525A (en) | Amino-functionalized single-walled carbon nanotube modified polyamide nanofiltration membrane as well as preparation method and application thereof | |
| CN107433143B (en) | Polyelectrolyte-loaded antibacterial cellulose nanofiltration membrane and preparation method thereof | |
| CN104941466A (en) | Preparation method of mesoporous carbon organic composite film for removing macromolecular hepatotoxins in water | |
| CN104128099A (en) | Composite nano-filtration membrane based on technologies of electrostatic spinning and self assembling and preparation method thereof | |
| CN107174950A (en) | The positive osmosis composite membrane of high-performance and preparation method that a kind of graphene oxide is modified | |
| CN105582816A (en) | Preparation method of forward osmosis membrane modified with oxidized graphene | |
| CN116020280A (en) | A preparation method for anti-wetting, anti-fouling and anti-fouling hydrogel Janus membrane | |
| CN111420563A (en) | Hybrid composite reverse osmosis/nanofiltration membrane, preparation method and application thereof | |
| CN114984779A (en) | Preparation method of high-flux cellulose forward osmosis membrane | |
| CN104107641B (en) | Forward osmosis organic-inorganic composite membrane and preparation method thereof | |
| CN114016285B (en) | Preparation method of functional nanofiber membrane for seawater desalination | |
| CN116371209A (en) | A kind of sodium alginate/chitosan composite nanofiltration membrane and its preparation method and application |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20220902 |
