[go: up one dir, main page]

CN115105953A - A kind of preparation method based on anionic surfactant/UIO-66 derived carbon composite nanofiltration membrane - Google Patents

A kind of preparation method based on anionic surfactant/UIO-66 derived carbon composite nanofiltration membrane Download PDF

Info

Publication number
CN115105953A
CN115105953A CN202210553557.2A CN202210553557A CN115105953A CN 115105953 A CN115105953 A CN 115105953A CN 202210553557 A CN202210553557 A CN 202210553557A CN 115105953 A CN115105953 A CN 115105953A
Authority
CN
China
Prior art keywords
uio
anionic surfactant
nanofiltration membrane
nanoparticles
composite nanofiltration
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.)
Granted
Application number
CN202210553557.2A
Other languages
Chinese (zh)
Other versions
CN115105953B (en
Inventor
王海涛
霍晓文
常娜
邵伟
贾彦军
荆兆敬
郭紫阳
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tianjin Polytechnic University
Original Assignee
Tianjin Polytechnic University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Tianjin Polytechnic University filed Critical Tianjin Polytechnic University
Priority to CN202210553557.2A priority Critical patent/CN115105953B/en
Publication of CN115105953A publication Critical patent/CN115105953A/en
Application granted granted Critical
Publication of CN115105953B publication Critical patent/CN115105953B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/02Reverse osmosis; Hyperfiltration ; Nanofiltration
    • B01D61/027Nanofiltration
    • 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
    • B01D69/12Composite membranes; Ultra-thin membranes
    • B01D69/125In situ manufacturing by polymerisation, polycondensation, cross-linking or chemical reaction
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/26Electrical properties
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Nanotechnology (AREA)
  • Water Supply & Treatment (AREA)
  • Inorganic Chemistry (AREA)
  • Manufacturing & Machinery (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The invention discloses a preparation method of a carbon composite nanofiltration membrane based on an anionic surfactant/UIO-66 derivative, which comprises the following steps: 1) mixing terephthalic acid solution, zirconium chloride salt solution and glacial acetic acid for reaction to obtain UIO-66; 2) calcining UIO-66 to obtain ZrO 2 A nanoparticle; 3) ZrO washed and dried with hydrofluoric acid 2 Nanoparticles to give C-UIO-66 nanoparticles; 4) dispersing the C-UIO-66 nano particles in an aqueous solution containing an anionic surfactant to obtain an anionic surfactant/C-UIO-66 suspension; 5) carrying out suction filtration on the suspension on the surface of a polysulfone membrane to obtain a C-PSF composite ultrafiltration membrane; 6) carrying out interfacial polymerization on the C-PSF composite ultrafiltration membrane,the composite nanofiltration membrane is prepared. The prepared composite nanofiltration membrane PA has the advantages of thin and uniform layer thickness, large effective permeation area, higher divalent salt rejection rate and higher permeation flux.

Description

一种基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制 备方法Preparation of a composite nanofiltration membrane based on anionic surfactant/UIO-66 derived carbon backup method

技术领域technical field

本发明涉及纳滤膜制备技术领域,特别是涉及一种基于阴离子表面活性剂/UIO-66衍生 碳复合纳滤膜的制备方法。The present invention relates to the technical field of nanofiltration membrane preparation, in particular to a preparation method based on anionic surfactant/UIO-66 derived carbon composite nanofiltration membrane.

背景技术Background technique

用于去除多价盐和小分子染料的纳滤(NF)膜,已广泛应用于污水处理、市政供水、分 盐以及染料脱除等领域。目前,较为成熟的纳滤膜制备工艺是通过界面聚合反应(IP)在超 滤/微滤(UF/MF)基底上形成聚酰胺选择层以制备薄膜复合(TFC)膜。然而,由于“tradeoff(权衡)”效应的影响,虽然TFC膜对多价盐离子具有较好的截留效果,但是水渗透性较低,使NF膜的推广应用受到限制。Nanofiltration (NF) membranes for removal of polyvalent salts and small molecule dyes have been widely used in sewage treatment, municipal water supply, salt separation and dye removal. At present, a relatively mature nanofiltration membrane preparation process is to form a polyamide selective layer on an ultrafiltration/microfiltration (UF/MF) substrate through interfacial polymerization (IP) to prepare a thin film composite (TFC) membrane. However, due to the "tradeoff" effect, although the TFC membrane has a good interception effect on polyvalent salt ions, the water permeability is low, which limits the popularization and application of NF membranes.

界面聚合成膜是基于Schotten-Baumann(肖滕-鲍曼)反应,在水/有机界面上进行PIP (哌嗪)/水相和TMC(1,3,5-苯三甲酰氯)/有机相之间的不可逆生长聚合,这种不受控制 且速度极快的反应很容易产生较厚的PA(聚酰胺)层(100-200nm)。一种可行的改性方法是添加纳米多孔材料,如MOF(金属-有机骨架)、碳纳米管和COF(覆晶薄膜)等,具有 合适孔径的纳米多孔材料会在PA层中形成利于水分子通过的传输通道,在保持无机盐截留 率基本不变的前提下较大程度的提升渗透性能。然而,纳米多孔材料的过量加入势必会引起 非选择性缺陷的产生,且对于具有羧酸配体的MOF材料,存在水稳定性和耐碱性差的问题, 极大地限制了MOF材料在纳滤膜制备中的作用。The interfacial polymerization film formation is based on the Schotten-Baumann (Schotten-Baumann) reaction, where PIP (piperazine)/aqueous phase and TMC (1,3,5-benzenetricarbonyl chloride)/organic phase are carried out at the water/organic interface. This uncontrolled and extremely fast reaction easily yields thick PA (polyamide) layers (100-200 nm). A feasible modification method is to add nanoporous materials, such as MOFs (metal-organic frameworks), carbon nanotubes, and COFs (chip-on-chip films), etc. Nanoporous materials with suitable pore size will form in the PA layer that is conducive to water molecules. Through the transmission channel, the permeability can be greatly improved on the premise that the retention rate of inorganic salts remains basically unchanged. However, the excessive addition of nanoporous materials will inevitably lead to the generation of non-selective defects, and for MOF materials with carboxylic acid ligands, there are problems of poor water stability and alkali resistance, which greatly limits the application of MOF materials in nanofiltration membranes. role in preparation.

近年来,一些MOF被用作前驱体,在保持原有形态和结构的同时,具有制备尺寸可控 的衍生碳纳米材料已被广泛应用于吸附、催化和电化学等领域。然而,MOF衍生碳材料在纳滤膜领域的应用未见相关报道。此外,Zr基金属有机框架UIO-66由于较好的八面体结构和合适的孔道直径作为常用的膜改性纳米材料一直是研究的热点。In recent years, some MOFs have been used as precursors, which have been widely used in adsorption, catalysis, and electrochemistry. However, the application of MOF-derived carbon materials in the field of nanofiltration membranes has not been reported. In addition, Zr-based metal-organic framework UIO-66 has been a research hotspot as a commonly used membrane-modified nanomaterial due to its good octahedral structure and suitable pore diameter.

发明内容SUMMARY OF THE INVENTION

本发明为解决现有技术中纳滤膜水通量较低的问题,提供了一种基于阴离子表面活性剂 /UIO-66衍生碳复合纳滤膜的制备方法,该方法将UIO-66衍生碳纳米材料应用于纳滤膜制备 领域,并采用将UIO-66衍生碳纳米颗粒经阴离子表面活性剂修饰后制备C-TFC复合纳滤膜, 使得由该方法制备的高性能复合纳滤膜的PA层厚度较薄且均匀,且分离层上具有较多褶皱 形貌,有效渗透面积大,与未引入阴离子表面活性剂/UIO-66衍生碳纳米颗粒的纳滤膜相比, 在保证二价盐截留率的情况下具有更大的渗透通量和优异的无机盐分离性能,突破了传统的 “trade off”效应,为高性能纳滤膜的制备提供了新途径,使其在膜分离技术领域具有良好 的应用价值和前景。In order to solve the problem of low water flux of nanofiltration membrane in the prior art, the present invention provides a preparation method based on anionic surfactant/UIO-66 derived carbon composite nanofiltration membrane. Nanomaterials are used in the field of nanofiltration membrane preparation, and UIO-66-derived carbon nanoparticles are modified with anionic surfactants to prepare C-TFC composite nanofiltration membranes, so that the PA of the high-performance composite nanofiltration membranes prepared by this method is The layer thickness is thin and uniform, and the separation layer has more folded morphology, and the effective permeation area is large. It has a larger permeation flux and excellent inorganic salt separation performance under the condition of rejection rate, which breaks through the traditional "trade off" effect and provides a new way for the preparation of high-performance nanofiltration membranes, making it in the field of membrane separation technology. It has good application value and prospect.

本发明是这样实现的,一种基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方 法,包括如下步骤:The present invention is realized like this, a kind of preparation method based on anionic surfactant/UIO-66 derivative carbon composite nanofiltration membrane, comprises the steps:

(1)将对苯二甲酸溶液、氯化锆盐溶液和冰乙酸混合反应,得到UIO-66;(1) mixed reaction of terephthalic acid solution, zirconium chloride salt solution and glacial acetic acid to obtain UIO-66;

(2)在一定温度下煅烧所述UIO-66,得到ZrO2纳米颗粒;( 2 ) calcining the UIO-66 at a certain temperature to obtain ZrO nanoparticles;

(3)将ZrO2纳米颗粒通过氢氟酸洗涤、干燥,得到UIO-66衍生碳纳米颗粒;( 3 ) washing and drying the ZrO nanoparticles by hydrofluoric acid to obtain UIO-66-derived carbon nanoparticles;

(4)将UIO-66衍生碳纳米颗粒分散于含有阴离子表面活性剂的水溶液中,得到阴离子 表面活性剂/C-UIO-66悬浮液;(4) UIO-66 derivative carbon nanoparticles are dispersed in the aqueous solution containing anionic surfactant to obtain anionic surfactant/C-UIO-66 suspension;

(5)将所述阴离子表面活性剂/C-UIO-66悬浮液抽滤在聚砜(PSF)膜表面,得到C-PSF 复合超滤膜;(5) suction filtration of the anionic surfactant/C-UIO-66 suspension on the surface of a polysulfone (PSF) membrane to obtain a C-PSF composite ultrafiltration membrane;

(6)在C-PSF复合超滤膜上进行界面聚合反应,制得所述基于阴离子表面活性剂 /UIO-66衍生碳的复合纳滤膜。(6) performing interfacial polymerization on the C-PSF composite ultrafiltration membrane to obtain the composite nanofiltration membrane based on anionic surfactant/UIO-66 derived carbon.

在本发明中,为了提高纳滤膜的渗透通量和稳定性,将UIO-66纳米颗粒在高温下煅烧, 经酸洗后得到具有正八面体形貌的UIO-66衍生碳纳米颗粒,经阴离子表面活性剂修饰后, 通过抽滤的方式预沉积在PSF基膜表面上,最后在负载C-UIO-66纳米颗粒的PSF膜表面进 行界面聚合反应制备C-TFC复合纳滤膜。本发明的优势在于:(1)将UIO-66衍生碳纳米材 料用于分离膜制备,在保持UIO-66原有形态、结构以及尺寸可控等优点外,较好的避免了 UIO-66纳米材料在溶液中容易水解的问题;(2)带有电负性的阴离子表面活性剂/C-UIO-66 纳米颗粒通过影响水相单体释放速率从而控制界面聚合反应,使得制备的复合纳滤膜具有较 薄的PA层;(3)C-UIO-66纳米颗粒的预沉积为界面聚合提供了粗糙的基底,使得制备的纳 滤膜PA层具有较多的褶皱结构,从而提升了有效渗透面积。In the present invention, in order to improve the permeation flux and stability of the nanofiltration membrane, UIO-66 nanoparticles are calcined at high temperature, and after acid washing, UIO-66 derived carbon nanoparticles with regular octahedral morphology are obtained. After the surfactant was modified, it was pre-deposited on the surface of the PSF base membrane by suction filtration, and finally the C-TFC composite nanofiltration membrane was prepared by interfacial polymerization on the surface of the PSF membrane loaded with C-UIO-66 nanoparticles. The advantages of the present invention are: (1) UIO-66-derived carbon nanomaterials are used for the preparation of separation membranes, in addition to the advantages of maintaining the original shape, structure and size of UIO-66, and better avoiding UIO-66 nanometers The problem that the material is easy to hydrolyze in solution; (2) the anionic surfactant/C-UIO-66 nanoparticles with electronegativity can control the interfacial polymerization by affecting the release rate of the monomer in the aqueous phase, so that the prepared composite nanofiltration The membrane has a thinner PA layer; (3) the pre-deposition of C-UIO-66 nanoparticles provides a rough substrate for interfacial polymerization, which makes the PA layer of the prepared nanofiltration membrane have more pleated structure, thereby improving the effective penetration area.

进一步地,所述步骤(1)中,对苯二甲酸溶液与氯化锆盐溶液的体积比为1:1,所述冰 乙酸的添加量与对苯二甲酸溶液和氯化锆盐溶液的混合液体积比为1:5~25;在水热温度为 120~160℃的恒温条件下水热反应8~20小时;Further, in the step (1), the volume ratio of the terephthalic acid solution and the zirconium chloride salt solution is 1:1, and the addition of the glacial acetic acid is the same as the terephthalic acid solution and the zirconium chloride salt solution. The volume ratio of the mixed solution is 1:5 to 25; the hydrothermal reaction is performed for 8 to 20 hours under the constant temperature of the hydrothermal temperature of 120 to 160 °C;

所制备的UIO-66纳米颗粒尺寸为60~400nm,UIO-66纳米颗粒为规则的八面体形貌。The prepared UIO-66 nanoparticles have a size of 60-400 nm, and the UIO-66 nanoparticles have regular octahedral morphology.

更进一步地,所述对苯二甲酸溶液为8mg/mL的二甲基甲酰胺(DMF)溶液,氯化锆盐溶液为6mg/mL的二甲基甲酰胺(DMF)溶液。Further, the terephthalic acid solution is 8 mg/mL dimethylformamide (DMF) solution, and the zirconium chloride salt solution is 6 mg/mL dimethylformamide (DMF) solution.

进一步地,所述步骤(2)中,在管式炉中N2气氛、600~1000℃温度下进行煅烧,升温 速率为5~8℃/min,煅烧时间为2~3小时。Further, in the step (2), calcination is carried out in a tube furnace in an N 2 atmosphere at a temperature of 600-1000° C., the heating rate is 5-8° C./min, and the calcination time is 2-3 hours.

进一步地,所述步骤(3)中,氢氟酸的洗涤时间为4~10小时,干燥温度为100~150℃, 所制备的UIO-66衍生碳(C-UIO-66)纳米颗粒粒径为50~350nm。Further, in the step (3), the washing time of hydrofluoric acid is 4-10 hours, the drying temperature is 100-150°C, and the prepared UIO-66-derived carbon (C-UIO-66) nanoparticles have a particle size of 50 to 350 nm.

进一步地,所述步骤(4)中,阴离子表面活性剂与UIO-66衍生碳纳米颗粒的质量比为 2.5~12.5:1。Further, in the step (4), the mass ratio of the anionic surfactant to the UIO-66-derived carbon nanoparticles is 2.5-12.5:1.

更进一步地,所述阴离子表面活性剂为十二烷基硫酸钠、十二烷基苯磺酸、十二烷基苯 磺酸钠、脂肪醇醚硫酸钠、α-烯基磺酸钠中的一种。Further, the anionic surfactant is sodium dodecyl sulfate, dodecylbenzenesulfonic acid, sodium dodecylbenzenesulfonate, sodium aliphatic alcohol ether sulfate, sodium α-alkenyl sulfonate. A sort of.

进一步地,所述步骤(5)中,悬浮液抽滤体积为5mL,抽滤压力为0.1Mpa。Further, in the step (5), the suction filtration volume of the suspension is 5 mL, and the suction filtration pressure is 0.1 Mpa.

进一步地,所述步骤(6)中,界面聚合反应所需水相单体哌嗪(PIP)浓度为0.5~2wt.%, 水相溶液为去离子水;油相单体1,3,5-苯三甲酰氯(TMC)浓度为0.05~0.2w/v.%,油相溶 液为正己烷;界面聚合反应时间为30~60s;Further, in the step (6), the concentration of the water phase monomer piperazine (PIP) required for the interfacial polymerization reaction is 0.5-2 wt.%, the water phase solution is deionized water; the oil phase monomers 1, 3, 5 -The concentration of trimellitic acid chloride (TMC) is 0.05~0.2w/v.%, the oil phase solution is n-hexane; the reaction time of interfacial polymerization is 30~60s;

所制备的复合纳滤膜的聚酰胺(PA)层厚度为20~45nm,在0.7MPa压力下,纯水通量达到47L-1·m-2·h-1以上,对Na2SO4的截留率保持在96%以上。The thickness of the polyamide (PA) layer of the prepared composite nanofiltration membrane is 20-45 nm, and under the pressure of 0.7 MPa, the pure water flux reaches more than 47 L -1 ·m -2 ·h -1 , and the resistance to Na 2 SO 4 is higher than that of Na 2 SO 4 . The retention rate remained above 96%.

一种基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜,采用上述制备方法制得。A composite nanofiltration membrane based on anionic surfactant/UIO-66 derived carbon is prepared by the above preparation method.

本发明具有的优点和积极效果是:The advantages and positive effects that the present invention has are:

1、本发明中,UIO-66纳米颗粒经过高温煅烧,氢氟酸洗涤后得到正八面体形貌的C-UIO-66纳米颗粒,解决了MOF材料在水相溶液尤其是碱性废水中容易水解的问题。1. In the present invention, UIO-66 nanoparticles are calcined at high temperature and washed with hydrofluoric acid to obtain C-UIO-66 nanoparticles with regular octahedral morphology, which solves the problem that MOF materials are easily hydrolyzed in aqueous solutions, especially alkaline wastewater. The problem.

2、本发明中,通过在预先沉积C-UIO-66的PSF基膜上进行界面聚合反应,由于C-UIO-66 本身的结构特性,使得可制备出具有褶皱形貌的PA层,显著增加了膜的有效渗透面积,提 高了膜的渗透通量。2. In the present invention, by performing interfacial polymerization on the PSF base film pre-deposited with C-UIO-66, due to the structural characteristics of C-UIO-66 itself, a PA layer with wrinkled morphology can be prepared, which significantly increases the The effective permeation area of the membrane is increased, and the permeation flux of the membrane is improved.

3、本发明中,由于C-UIO-66经过SDS修饰后具有较强的负电效应,在界面聚合过程中通过影响PIP单体的释放速率,从而控制界面聚合反应,使得制备了具有更薄PA层的复合纳滤膜。3. In the present invention, since C-UIO-66 has a strong negative effect after being modified by SDS, the interfacial polymerization is controlled by affecting the release rate of the PIP monomer during the interfacial polymerization process, so that a thinner PA is prepared. layered composite nanofiltration membrane.

附图说明Description of drawings

为了更清楚地说明本发明具体实施方式的技术方案,下面将对具体实施方式描述中所需 要使用的附图作简单的介绍,显而易见地,下面描述中的附图是本发明的一些具体实施方式, 对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其 他的附图。In order to illustrate the technical solutions of the specific embodiments of the present invention more clearly, the following will briefly introduce the accompanying drawings used in the description of the specific embodiments. Obviously, the accompanying drawings in the following description are some specific embodiments of the present invention. , For those of ordinary skill in the art, other drawings can also be obtained from these drawings without any creative effort.

图1是根据本发明制得的扫描电镜图;其中,(a)为对比例,(b)为实施例4。1 is a scanning electron microscope image prepared according to the present invention; wherein, (a) is a comparative example, and (b) is Example 4.

具体实施方式Detailed ways

下面将结合附图对本发明的技术方案进行清楚、完整地描述,显然,所描述的实施例是 本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员 在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The technical solutions of the present invention will be clearly and completely described below with reference to the accompanying drawings. Obviously, the described embodiments are part of the embodiments of the present invention, but not all of the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those of ordinary skill in the art without creative efforts shall fall within the protection scope of the present invention.

本实施例提供了一种基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,包 括如下步骤:The present embodiment provides a kind of preparation method based on anionic surfactant/UIO-66 derivative carbon composite nanofiltration membrane, comprises the steps:

(1)将对苯二甲酸溶液、氯化锆盐溶液和冰乙酸混合反应,得到UIO-66;(1) mixed reaction of terephthalic acid solution, zirconium chloride salt solution and glacial acetic acid to obtain UIO-66;

(2)在一定温度下煅烧所述UIO-66,得到ZrO2纳米颗粒;( 2 ) calcining the UIO-66 at a certain temperature to obtain ZrO nanoparticles;

(3)将ZrO2纳米颗粒通过氢氟酸洗涤、干燥,得到UIO-66衍生碳(C-UIO-66)纳米颗粒;( 3 ) washing and drying the ZrO2 nanoparticles by hydrofluoric acid to obtain UIO-66-derived carbon (C-UIO-66) nanoparticles;

(4)将UIO-66衍生碳纳米颗粒分散于含有阴离子表面活性剂的水溶液中,得到阴离子 表面活性剂/C-UIO-66悬浮液;(4) UIO-66 derivative carbon nanoparticles are dispersed in the aqueous solution containing anionic surfactant to obtain anionic surfactant/C-UIO-66 suspension;

(5)将所述阴离子表面活性剂/C-UIO-66悬浮液抽滤在聚砜(PSF)膜表面,得到C-PSF 复合超滤膜;(5) suction filtration of the anionic surfactant/C-UIO-66 suspension on the surface of a polysulfone (PSF) membrane to obtain a C-PSF composite ultrafiltration membrane;

(6)在C-PSF复合超滤膜上进行界面聚合反应,制得所述基于阴离子表面活性剂 /UIO-66衍生碳的复合纳滤膜。(6) performing interfacial polymerization on the C-PSF composite ultrafiltration membrane to obtain the composite nanofiltration membrane based on anionic surfactant/UIO-66 derived carbon.

所述步骤(1)中,对苯二甲酸溶液与氯化锆盐溶液的体积比为1:1,所述冰乙酸的添加 量与对苯二甲酸溶液和氯化锆盐溶液的混合液体积比为1:5~25,优选1:20。In the described step (1), the volume ratio of the terephthalic acid solution and the zirconium chloride salt solution is 1:1, and the addition of the glacial acetic acid is the volume of the mixed solution of the terephthalic acid solution and the zirconium chloride salt solution. The ratio is 1:5 to 25, preferably 1:20.

在水热温度为120~160℃的恒温条件下水热反应8~20小时,优选水热温度为150℃, 水热时间为12小时。所制备的UIO-66纳米颗粒尺寸为60~400nm,UIO-66纳米颗粒为规则的八面体形貌。The hydrothermal reaction is carried out for 8 to 20 hours under the constant temperature of the hydrothermal temperature of 120-160°C, preferably the hydrothermal temperature is 150°C, and the hydrothermal time is 12 hours. The prepared UIO-66 nanoparticles have a size of 60-400 nm, and the UIO-66 nanoparticles have regular octahedral morphology.

对苯二甲酸溶液为8mg/mL的二甲基甲酰胺(DMF)溶液,氯化锆盐溶液为6mg/mL 的二甲基甲酰胺(DMF)溶液。The terephthalic acid solution was 8 mg/mL in dimethylformamide (DMF), and the zirconium chloride salt solution was 6 mg/mL in dimethylformamide (DMF).

所述步骤(2)中,在管式炉中N2气氛、600~1000℃温度下进行煅烧,优选800℃;升温速率为5~8℃/min,煅烧时间为2~3小时。In the step (2), calcination is carried out in a tube furnace under N2 atmosphere at a temperature of 600-1000°C, preferably 800°C; the heating rate is 5-8°C/min, and the calcination time is 2-3 hours.

所述步骤(3)中,氢氟酸的洗涤时间为4~10小时,优选6小时;干燥温度为100~150℃, 所制备的UIO-66衍生碳纳米颗粒粒径为50~350nm。In the step (3), the washing time of hydrofluoric acid is 4-10 hours, preferably 6 hours; the drying temperature is 100-150°C, and the prepared UIO-66-derived carbon nanoparticles have a particle size of 50-350 nm.

所述步骤(4)中,阴离子表面活性剂与UIO-66衍生碳纳米颗粒的质量比为2.5~12.5: 1,优选5:1。In the step (4), the mass ratio of the anionic surfactant to the UIO-66-derived carbon nanoparticles is 2.5-12.5:1, preferably 5:1.

阴离子表面活性剂为十二烷基硫酸钠、十二烷基苯磺酸、十二烷基苯磺酸钠、脂肪醇醚 硫酸钠、α-烯基磺酸钠中的一种,优选为十二烷基硫酸钠(SDS)。The anionic surfactant is one of sodium dodecyl sulfate, dodecylbenzenesulfonic acid, sodium dodecylbenzenesulfonate, sodium aliphatic alcohol ether sulfate, and sodium α-alkenyl sulfonate, preferably ten Sodium Dialkyl Sulfate (SDS).

所述步骤(5)中,悬浮液抽滤体积为5mL,抽滤压力为0.1Mpa。In the step (5), the suction filtration volume of the suspension was 5 mL, and the suction filtration pressure was 0.1 Mpa.

所述步骤(6)中,界面聚合反应所需水相单体哌嗪(PIP)浓度为0.5~2wt.%,优选1 wt.%;油相单体1,3,5-苯三甲酰氯(TMC)浓度为0.05~0.2w/v.%,优选0.15w/v.%;水相 溶液为去离子水,油相溶液为正己烷;界面聚合反应时间为30~60s。In the step (6), the concentration of the water phase monomer piperazine (PIP) required for the interfacial polymerization reaction is 0.5-2 wt.%, preferably 1 wt.%; the oil phase monomer 1,3,5-benzenetricarbonyl chloride ( TMC) concentration is 0.05~0.2w/v.%, preferably 0.15w/v.%; the water phase solution is deionized water, the oil phase solution is n-hexane; the interfacial polymerization reaction time is 30~60s.

所制备的复合纳滤膜的聚酰胺(PA)层厚度为20~45nm,在0.7MPa压力下,纯水通量达到47L-1·m-2·h-1以上,对Na2SO4的截留率保持在96%以上。The thickness of the polyamide (PA) layer of the prepared composite nanofiltration membrane is 20-45 nm, and under the pressure of 0.7 MPa, the pure water flux reaches more than 47 L -1 ·m -2 ·h -1 , and the resistance to Na 2 SO 4 is higher than that of Na 2 SO 4 . The retention rate remained above 96%.

预先沉积的阴离子表面活性剂/C-UIO-66纳米颗粒会吸附水相溶液中的PIP,之后加入 油相溶液,PIP向油相扩散速率减慢,使得生成更薄的PA层;另一方面,凸起的C-UIO-66 纳米颗粒也会使得PA层形貌具有褶皱,从而制备出具有较薄PA层且PA层上含有更多褶皱 结构的复合纳滤膜。The pre-deposited anionic surfactant/C-UIO-66 nanoparticles will adsorb the PIP in the aqueous phase solution, and then add the oil phase solution, the diffusion rate of PIP to the oil phase slows down, resulting in a thinner PA layer; on the other hand , the raised C-UIO-66 nanoparticles will also make the PA layer morphology wrinkled, thereby preparing a composite nanofiltration membrane with a thinner PA layer and more wrinkled structures on the PA layer.

为了更好地理解本发明的上述实施方式,下面结合具体示例对其进行进一步说明。In order to better understand the above-mentioned embodiments of the present invention, they are further described below with reference to specific examples.

下述实施例及对比例中:In the following examples and comparative examples:

对苯二甲酸,分析纯,购自上海阿拉丁生化科技股份有限公司;Terephthalic acid, analytically pure, was purchased from Shanghai Aladdin Biochemical Technology Co., Ltd.;

氯化锆(ZrCl4),分析纯,购自上海阿拉丁生化科技股份有限公司;Zirconium chloride (ZrCl 4 ), analytically pure, purchased from Shanghai Aladdin Biochemical Technology Co., Ltd.;

十二烷基硫酸钠(SDS),分析纯,购自上海毕得医药科技有限公司;Sodium dodecyl sulfate (SDS), analytical grade, purchased from Shanghai Bide Pharmaceutical Technology Co., Ltd.;

无水哌嗪(PIP),分析纯,购自上海阿拉丁生化科技股份有限公司;Anhydrous piperazine (PIP), analytically pure, was purchased from Shanghai Aladdin Biochemical Technology Co., Ltd.;

1,3,5-苯三甲酰氯(TMC),分析纯,购自北京百灵威科技有限公司;1,3,5-benzenetricarbonyl chloride (TMC), analytical grade, purchased from Beijing Bailingwei Technology Co., Ltd.;

冰乙酸(AA),分析纯,购自上海阿拉丁生化科技股份有限公司;Glacial acetic acid (AA), analytical grade, was purchased from Shanghai Aladdin Biochemical Technology Co., Ltd.;

正己烷,分析纯,购自天津科密欧化学试剂有限公司;n-Hexane, analytical grade, purchased from Tianjin Kemeiou Chemical Reagent Co., Ltd.;

二甲基甲酰胺,分析纯,购自天津科密欧化学试剂有限公司。Dimethylformamide, analytical grade, was purchased from Tianjin Kemeiou Chemical Reagent Co., Ltd.

实施例1Example 1

(1)将对苯二甲酸(0.16g)的DMF溶液(20mL)与氯化锆盐(0.12g)的DMF溶液(20mL)和冰乙酸(2mL)混合,在150℃恒温条件下水热反应12小时。完成后,将所 有混合物离心分离,并用DMF和乙醇各洗涤3次,在120℃下干燥,得到UIO-66;(1) Mix a DMF solution (20 mL) of terephthalic acid (0.16 g) with a DMF solution (20 mL) of zirconium chloride salt (0.12 g) and glacial acetic acid (2 mL), and conduct a hydrothermal reaction at a constant temperature of 150°C for 12 Hour. After completion, all mixtures were centrifuged, washed three times each with DMF and ethanol, and dried at 120°C to obtain UIO-66;

(2)在管式炉中N2气氛、800℃的温度下煅烧步骤(1)得到的UIO-66,煅烧时间为2小时,得到ZrO2纳米颗粒;(2) calcining the UIO-66 obtained in step (1) at a temperature of 800° C. in an N atmosphere in a tube furnace for 2 hours to obtain ZrO nanoparticles ;

(3)将步骤(2)得到的ZrO2纳米颗粒通过氢氟酸洗涤6小时,100℃下干燥10小时,得到C-UIO-66纳米颗粒;(3) washing the ZrO nanoparticles obtained in step ( 2 ) with hydrofluoric acid for 6 hours and drying at 100° C. for 10 hours to obtain C-UIO-66 nanoparticles;

(4)将C-UIO-66纳米颗粒(5mg)分散于含有十二烷基硫酸钠(50mg)的水溶液(200mL)中,得到SDS/C-UIO-66悬浮液;(4) C-UIO-66 nanoparticles (5 mg) were dispersed in an aqueous solution (200 mL) containing sodium dodecyl sulfate (50 mg) to obtain SDS/C-UIO-66 suspension;

(5)将SDS/C-UIO-66悬浮液(5mL)在压力为0.1Mpa下抽滤在聚砜(PSF)膜表面, 得到C-PSF复合超滤膜;(5) suction filtration of the SDS/C-UIO-66 suspension (5 mL) on the surface of a polysulfone (PSF) membrane under a pressure of 0.1 Mpa to obtain a C-PSF composite ultrafiltration membrane;

(6)以PIP(1wt.%)为水相单体,TMC(0.15w/v.%)为油相单体,在所述C-PSF复 合超滤膜上进行界面聚合反应,聚合时间为1分钟,制得所述基于SDS/UIO-66衍生碳的复 合纳滤膜。(6) Using PIP (1wt.%) as the water phase monomer and TMC (0.15w/v.%) as the oil phase monomer, perform interfacial polymerization on the C-PSF composite ultrafiltration membrane, and the polymerization time is In 1 minute, the composite nanofiltration membrane based on SDS/UIO-66-derived carbon was prepared.

实施例2Example 2

(1)将对苯二甲酸(0.16g)的DMF溶液(20mL)与氯化锆盐(0.12g)的DMF溶液(20mL)和冰乙酸(2mL)混合,在150℃恒温条件下水热反应12小时。完成后,将所 有混合物离心分离,并用DMF和乙醇各洗涤3次,在120℃下干燥,得到UIO-66;(1) Mix a DMF solution (20 mL) of terephthalic acid (0.16 g) with a DMF solution (20 mL) of zirconium chloride salt (0.12 g) and glacial acetic acid (2 mL), and conduct a hydrothermal reaction at a constant temperature of 150°C for 12 Hour. After completion, all mixtures were centrifuged, washed three times each with DMF and ethanol, and dried at 120°C to obtain UIO-66;

(2)在管式炉中N2气氛、800℃的温度下煅烧步骤(1)得到的UIO-66,煅烧时间为2小时,得到ZrO2纳米颗粒;(2) calcining the UIO-66 obtained in step (1) at a temperature of 800° C. in an N atmosphere in a tube furnace for 2 hours to obtain ZrO nanoparticles ;

(3)将步骤(2)得到的ZrO2纳米颗粒通过氢氟酸洗涤6小时,100℃下干燥10小时,得到C-UIO-66纳米颗粒;(3) washing the ZrO nanoparticles obtained in step ( 2 ) with hydrofluoric acid for 6 hours and drying at 100° C. for 10 hours to obtain C-UIO-66 nanoparticles;

(4)将C-UIO-66纳米颗粒(4mg)分散于含有十二烷基硫酸钠(50mg)的水溶液(200mL)中,得到SDS/C-UIO-66悬浮液;(4) C-UIO-66 nanoparticles (4 mg) were dispersed in an aqueous solution (200 mL) containing sodium dodecyl sulfate (50 mg) to obtain SDS/C-UIO-66 suspension;

(5)将SDS/C-UIO-66悬浮液(5mL)在压力为0.1Mpa下抽滤在聚砜(PSF)膜表面, 得到C-PSF复合超滤膜;(5) suction filtration of the SDS/C-UIO-66 suspension (5 mL) on the surface of a polysulfone (PSF) membrane under a pressure of 0.1 Mpa to obtain a C-PSF composite ultrafiltration membrane;

(6)以PIP(1wt.%)为水相单体,TMC(0.15w/v.%)为油相单体,在所述C-PSF复 合超滤膜上进行界面聚合反应,聚合时间为1分钟,制得所述基于SDS/UIO-66衍生碳的复 合纳滤膜。(6) Using PIP (1wt.%) as the water phase monomer and TMC (0.15w/v.%) as the oil phase monomer, perform interfacial polymerization on the C-PSF composite ultrafiltration membrane, and the polymerization time is In 1 minute, the composite nanofiltration membrane based on SDS/UIO-66-derived carbon was prepared.

实施例3Example 3

(1)将对苯二甲酸(0.16g)的DMF溶液(20mL)与氯化锆盐(0.12g)的DMF溶液(20mL)和冰乙酸(4mL)混合,在150℃恒温条件下水热反应12小时。完成后,将所 有混合物离心分离,并用DMF和乙醇各洗涤3次,在120℃下干燥,得到UIO-66;(1) Mix a DMF solution (20 mL) of terephthalic acid (0.16 g) with a DMF solution (20 mL) of zirconium chloride salt (0.12 g) and glacial acetic acid (4 mL), and perform a hydrothermal reaction at a constant temperature of 150°C for 12 Hour. After completion, all mixtures were centrifuged, washed three times each with DMF and ethanol, and dried at 120°C to obtain UIO-66;

(2)在管式炉中N2气氛、800℃的温度下煅烧步骤(1)得到的UIO-66,煅烧时间为2小时,得到ZrO2纳米颗粒;(2) calcining the UIO-66 obtained in step (1) at a temperature of 800° C. in an N atmosphere in a tube furnace for 2 hours to obtain ZrO nanoparticles ;

(3)将步骤(2)得到的ZrO2纳米颗粒通过氢氟酸洗涤6小时,100℃下干燥10小时,得到C-UIO-66纳米颗粒;(3) washing the ZrO nanoparticles obtained in step ( 2 ) with hydrofluoric acid for 6 hours and drying at 100° C. for 10 hours to obtain C-UIO-66 nanoparticles;

(4)将C-UIO-66纳米颗粒(20mg)分散于含有十二烷基硫酸钠(50mg)的水溶液(200mL)中,得到SDS/C-UIO-66悬浮液;(4) Disperse C-UIO-66 nanoparticles (20 mg) in an aqueous solution (200 mL) containing sodium dodecyl sulfate (50 mg) to obtain SDS/C-UIO-66 suspension;

(5)将SDS/C-UIO-66悬浮液(5mL)在压力为0.1Mpa下抽滤在聚砜(PSF)膜表面, 得到C-PSF复合超滤膜;(5) suction filtration of the SDS/C-UIO-66 suspension (5 mL) on the surface of a polysulfone (PSF) membrane under a pressure of 0.1 Mpa to obtain a C-PSF composite ultrafiltration membrane;

(6)以PIP(1wt.%)为水相单体,TMC(0.15w/v.%)为油相单体,在所述C-PSF复 合超滤膜上进行界面聚合反应,聚合时间为1分钟,制得所述基于SDS/UIO-66衍生碳的复 合纳滤膜。(6) Using PIP (1wt.%) as the water phase monomer and TMC (0.15w/v.%) as the oil phase monomer, perform interfacial polymerization on the C-PSF composite ultrafiltration membrane, and the polymerization time is In 1 minute, the composite nanofiltration membrane based on SDS/UIO-66-derived carbon was prepared.

实施例4Example 4

(1)将对苯二甲酸(0.16g)的DMF溶液(20mL)与氯化锆盐(0.12g)的DMF溶液(20mL)和冰乙酸(4mL)混合,在150℃恒温条件下水热反应12小时。完成后,将所 有混合物离心分离,并用DMF和乙醇各洗涤3次,在120℃下干燥,得到UIO-66;(1) Mix a DMF solution (20 mL) of terephthalic acid (0.16 g) with a DMF solution (20 mL) of zirconium chloride salt (0.12 g) and glacial acetic acid (4 mL), and perform a hydrothermal reaction at a constant temperature of 150°C for 12 Hour. After completion, all mixtures were centrifuged, washed three times each with DMF and ethanol, and dried at 120°C to obtain UIO-66;

(2)在管式炉中N2气氛、800℃的温度下煅烧步骤(1)得到的UIO-66,煅烧时间为2小时,得到ZrO2纳米颗粒;(2) calcining the UIO-66 obtained in step (1) at a temperature of 800° C. in an N atmosphere in a tube furnace for 2 hours to obtain ZrO nanoparticles ;

(3)将步骤(2)得到的ZrO2纳米颗粒通过氢氟酸洗涤6小时,100℃下干燥10小时,得到C-UIO-66纳米颗粒;(3) washing the ZrO nanoparticles obtained in step ( 2 ) with hydrofluoric acid for 6 hours and drying at 100° C. for 10 hours to obtain C-UIO-66 nanoparticles;

(4)将C-UIO-66纳米颗粒(10mg)分散于含有十二烷基硫酸钠(50mg)的水溶液(200mL)中,得到SDS/C-UIO-66悬浮液;(4) C-UIO-66 nanoparticles (10 mg) were dispersed in an aqueous solution (200 mL) containing sodium dodecyl sulfate (50 mg) to obtain SDS/C-UIO-66 suspension;

(5)将SDS/C-UIO-66悬浮液(5mL)在压力为0.1Mpa下抽滤在聚砜(PSF)膜表面, 得到C-PSF复合超滤膜;(5) suction filtration of the SDS/C-UIO-66 suspension (5 mL) on the surface of a polysulfone (PSF) membrane under a pressure of 0.1 Mpa to obtain a C-PSF composite ultrafiltration membrane;

(6)以PIP(1wt.%)为水相单体,TMC(0.15w/v.%)为油相单体,在所述C-PSF复 合超滤膜上进行界面聚合反应,聚合时间为1分钟,制得所述基于SDS/UIO-66衍生碳的复 合纳滤膜。(6) Using PIP (1wt.%) as the water phase monomer and TMC (0.15w/v.%) as the oil phase monomer, perform interfacial polymerization on the C-PSF composite ultrafiltration membrane, and the polymerization time is In 1 minute, the composite nanofiltration membrane based on SDS/UIO-66-derived carbon was prepared.

对比例Comparative ratio

仅采用与实施例1~4中步骤(6)相同的方式制得TFC纳滤膜,未引入C-UIO-66纳米颗粒。TFC纳滤膜的扫描电镜图如图1a所示。Only the TFC nanofiltration membrane was prepared in the same manner as step (6) in Examples 1 to 4, without introducing C-UIO-66 nanoparticles. The SEM image of the TFC nanofiltration membrane is shown in Fig. 1a.

性能测试Performance Testing

在本发明中,采用去离子水和Na2SO4溶液对实施例1-4及对比例所制得的复合纳滤膜 的膜通量及截留性能进行测试。具体地,取1g/L的Na2SO4溶液1L,在0.7Mpa驱动压力 下进行膜分离性能测试,利用电导率仪测试过滤液及原溶液的盐浓度。其结果如下表1所示。In the present invention, deionized water and Na 2 SO 4 solution were used to test the membrane flux and retention performance of the composite nanofiltration membranes prepared in Examples 1-4 and Comparative Examples. Specifically, take 1 L of 1 g/L Na 2 SO 4 solution, conduct the membrane separation performance test under a driving pressure of 0.7 Mpa, and use a conductivity meter to test the salt concentration of the filtrate and the original solution. The results are shown in Table 1 below.

表1复合纳滤膜分离性能及表征结果Table 1. Separation performance and characterization results of composite nanofiltration membrane

Figure BDA0003653998070000071
Figure BDA0003653998070000071

从表1的数据可知,对于脱盐能力,实施例1、2、3、4和对比例对Na2SO4都具有较高的截留性能,达到96%以上;对于膜通量,与对比例相比,实施例1、2、3、4均有大幅提 升,其中实施例4达到58.59L/m2·h,与对比例相比提升了114%;对于复合纳滤膜的PA 层厚度,由于SDS/UIO-66衍生碳复合纳滤膜本身的负电性质而对PIP具有较强的静电作用, 使得PA层厚度从对比例的144.29nm降低到32.45nm以下,从而显著降低了PA层的厚度; 另外,对于实施例1、2、3、4,由于在膜的中间层沉积了不同尺寸的UIO-66衍生碳纳米颗 粒,使得具有较大的表面粗糙度,进一步提升了复合纳滤膜的有效渗透面积。From the data in Table 1, it can be seen that for desalination capacity, Examples 1, 2, 3, 4 and the comparative example all have high rejection performance for Na 2 SO 4 , reaching more than 96%; for membrane flux, compared with the comparative example Compared with the comparative example, Examples 1, 2, 3, and 4 have all been greatly improved, among which Example 4 reached 58.59 L/m 2 ·h, an increase of 114% compared with the comparative example; for the thickness of the PA layer of the composite nanofiltration membrane, due to the The negative charge of the SDS/UIO-66-derived carbon composite nanofiltration membrane itself has a strong electrostatic effect on PIP, which reduces the thickness of the PA layer from 144.29 nm in the comparative example to below 32.45 nm, thereby significantly reducing the thickness of the PA layer; In addition, for Examples 1, 2, 3, and 4, due to the deposition of UIO-66-derived carbon nanoparticles of different sizes in the middle layer of the membrane, the surface roughness is larger, which further improves the effectiveness of the composite nanofiltration membrane. penetration area.

此外,参见图1b,其为本发明实施例4制得的基于SDS/UIO-66衍生碳的复合纳滤膜的 扫描电镜图。从图中可以看出,复合纳滤膜的PA层厚度明显小于对比例中传统TFC纳滤膜 的聚酰胺层厚度,因而能够缩短水分子传输路径,显著提升了膜的渗透通量。本发明其它实 施例制得的基于SDS/UIO-66衍生碳的复合纳滤膜的扫描电镜图与实施例4类似,因而将其 省略。In addition, see Figure 1b, which is a scanning electron microscope image of the composite nanofiltration membrane based on SDS/UIO-66-derived carbon prepared in Example 4 of the present invention. It can be seen from the figure that the thickness of the PA layer of the composite nanofiltration membrane is significantly smaller than that of the polyamide layer of the traditional TFC nanofiltration membrane in the comparative example, which can shorten the water molecule transmission path and significantly improve the permeation flux of the membrane. The scanning electron microscope images of the composite nanofiltration membranes based on SDS/UIO-66-derived carbon prepared in other embodiments of the present invention are similar to those in Example 4, so they are omitted.

最后应说明的是:以上各实施例仅用以说明本发明的技术方案,而非对其限制;尽管参 照前述各实施例对本发明进行了详细的说明,本领域的普通技术人员应当理解:其依然可以 对前述各实施例所记载的技术方案进行修改,或者对其中部分或者全部技术特征进行等同替 换;而这些修改或者替换,并不使相应技术方案的本质脱离本发明各实施例技术方案的范围。Finally, it should be noted that the above embodiments are only used to illustrate the technical solutions of the present invention, but not to limit them; although the present invention has been described in detail with reference to the foregoing embodiments, those of ordinary skill in the art should understand that: The technical solutions described in the foregoing embodiments can still be modified, or some or all of the technical features thereof can be equivalently replaced; and these modifications or replacements do not make the essence of the corresponding technical solutions deviate from the technical solutions of the embodiments of the present invention. scope.

Claims (10)

1.一种基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,包括如下步骤:1. a preparation method based on anionic surfactant/UIO-66 derivative carbon composite nanofiltration membrane, is characterized in that, comprises the steps: (1)将对苯二甲酸溶液、氯化锆盐溶液和冰乙酸混合反应,得到UIO-66;(1) mixed reaction of terephthalic acid solution, zirconium chloride salt solution and glacial acetic acid to obtain UIO-66; (2)在一定温度下煅烧所述UIO-66,得到ZrO2纳米颗粒;( 2 ) calcining the UIO-66 at a certain temperature to obtain ZrO nanoparticles; (3)将ZrO2纳米颗粒通过氢氟酸洗涤、干燥,得到UIO-66衍生碳纳米颗粒;( 3 ) washing and drying the ZrO nanoparticles by hydrofluoric acid to obtain UIO-66-derived carbon nanoparticles; (4)将UIO-66衍生碳纳米颗粒分散于含有阴离子表面活性剂的水溶液中,得到阴离子表面活性剂/C-UIO-66悬浮液;(4) dispersing the UIO-66-derived carbon nanoparticles in an aqueous solution containing an anionic surfactant to obtain an anionic surfactant/C-UIO-66 suspension; (5)将所述阴离子表面活性剂/C-UIO-66悬浮液抽滤在聚砜膜表面,得到C-PSF复合超滤膜;(5) suction filtration of the anionic surfactant/C-UIO-66 suspension on the surface of the polysulfone membrane to obtain a C-PSF composite ultrafiltration membrane; (6)在C-PSF复合超滤膜上进行界面聚合反应,制得所述基于阴离子表面活性剂/UIO-66衍生碳的复合纳滤膜。(6) performing interfacial polymerization on the C-PSF composite ultrafiltration membrane to prepare the composite nanofiltration membrane based on anionic surfactant/UIO-66-derived carbon. 2.根据权利要求1所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述步骤(1)中,对苯二甲酸溶液与氯化锆盐溶液的体积比为1:1,所述冰乙酸的添加量与对苯二甲酸溶液和氯化锆盐溶液的混合液体积比为1:5~25;在水热温度为120~160℃的恒温条件下水热反应8~20小时;2. the preparation method based on anionic surfactant/UIO-66 derivative carbon composite nanofiltration membrane according to claim 1, is characterized in that, in described step (1), terephthalic acid solution and zirconium chloride salt The volume ratio of the solution is 1:1, and the volume ratio of the added amount of the glacial acetic acid to the mixed solution of the terephthalic acid solution and the zirconium chloride salt solution is 1:5 to 25; Hydrothermal reaction under constant temperature conditions for 8 to 20 hours; 所制备的UIO-66纳米颗粒尺寸为60~400nm,UIO-66纳米颗粒为规则的八面体形貌。The prepared UIO-66 nanoparticles have a size of 60-400 nm, and the UIO-66 nanoparticles have regular octahedral morphology. 3.根据权利要求2所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述对苯二甲酸溶液为8mg/mL的二甲基甲酰胺溶液,氯化锆盐溶液为6mg/mL的二甲基甲酰胺溶液。3. the preparation method based on anionic surfactant/UIO-66 derivative carbon composite nanofiltration membrane according to claim 2, is characterized in that, described terephthalic acid solution is the dimethylformamide solution of 8mg/mL , the zirconium chloride salt solution is a 6 mg/mL solution of dimethylformamide. 4.根据权利要求1所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述步骤(2)中,在管式炉中N2气氛、600~1000℃温度下进行煅烧,升温速率为5~8℃/min,煅烧时间为2~3小时。4. the preparation method based on anionic surfactant/UIO-66 derived carbon composite nanofiltration membrane according to claim 1, is characterized in that, in described step ( 2 ), in tube furnace N atmosphere, 600 The calcination is carried out at a temperature of ~1000 °C, the heating rate is 5 to 8 °C/min, and the calcination time is 2 to 3 hours. 5.根据权利要求1所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述步骤(3)中,氢氟酸的洗涤时间为4~10小时,干燥温度为100~150℃,所制备的UIO-66衍生碳纳米颗粒粒径为50~350nm。5. The preparation method of anionic surfactant/UIO-66-derived carbon composite nanofiltration membrane according to claim 1, wherein in the step (3), the washing time of hydrofluoric acid is 4-10 hours, the drying temperature is 100-150° C., and the prepared UIO-66-derived carbon nanoparticles have a particle size of 50-350 nm. 6.根据权利要求1所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述步骤(4)中,阴离子表面活性剂与UIO-66衍生碳纳米颗粒的质量比为2.5~12.5:1。6. The preparation method of anionic surfactant/UIO-66 derived carbon composite nanofiltration membrane according to claim 1, wherein in the step (4), anionic surfactant and UIO-66 derived carbon The mass ratio of nanoparticles is 2.5-12.5:1. 7.根据权利要求6所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述阴离子表面活性剂为十二烷基硫酸钠、十二烷基苯磺酸、十二烷基苯磺酸钠、脂肪醇醚硫酸钠、α-烯基磺酸钠中的一种。7. the preparation method based on anionic surfactant/UIO-66 derived carbon composite nanofiltration membrane according to claim 6, is characterized in that, described anionic surfactant is sodium dodecyl sulfate, dodecyl One of benzenesulfonic acid, sodium dodecylbenzenesulfonate, sodium aliphatic alcohol ether sulfate, and sodium α-alkenylsulfonate. 8.根据权利要求1所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述步骤(5)中,悬浮液抽滤体积为5mL,抽滤压力为0.1Mpa。8. the preparation method based on anionic surfactant/UIO-66 derivative carbon composite nanofiltration membrane according to claim 1, is characterized in that, in described step (5), suspension suction filtration volume is 5mL, suction filtration The pressure is 0.1Mpa. 9.根据权利要求1所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法,其特征在于,所述步骤(6)中,界面聚合反应所需水相单体哌嗪浓度为0.5~2wt.%,水相溶液为去离子水;油相单体1,3,5-苯三甲酰氯浓度为0.05~0.2w/v.%,油相溶液为正己烷;界面聚合反应时间为30~60s;9. the preparation method based on anionic surfactant/UIO-66 derivative carbon composite nanofiltration membrane according to claim 1, is characterized in that, in described step (6), the required water phase monomer of interfacial polymerization reaction is piperidine The concentration of azine is 0.5~2wt.%, the water phase solution is deionized water; the concentration of oil phase monomer 1,3,5-benzenetricarboxylic acid chloride is 0.05~0.2w/v.%, the oil phase solution is n-hexane; the interfacial polymerization The reaction time is 30-60s; 所制备的复合纳滤膜的聚酰胺层厚度为20~45nm,在0.7MPa压力下,纯水通量达到47L-1·m-2·h-1以上,对Na2SO4的截留率保持在96%以上。The thickness of the polyamide layer of the prepared composite nanofiltration membrane is 20-45 nm. Under the pressure of 0.7 MPa, the pure water flux reaches more than 47 L -1 ·m -2 ·h -1 , and the rejection rate of Na 2 SO 4 is maintained. above 96%. 10.一种基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜,其特征在于,采用权利要求1-9中任一项所述的基于阴离子表面活性剂/UIO-66衍生碳复合纳滤膜的制备方法制得。10. A composite nanofiltration membrane based on anionic surfactant/UIO-66 derived carbon, characterized in that, using the composite nanofiltration membrane based on anionic surfactant/UIO-66 derived carbon according to any one of claims 1-9 The preparation method of the filter membrane is obtained.
CN202210553557.2A 2022-05-20 2022-05-20 Preparation method of carbon composite nanofiltration membrane based on anionic surfactant/UIO-66 derivative Active CN115105953B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210553557.2A CN115105953B (en) 2022-05-20 2022-05-20 Preparation method of carbon composite nanofiltration membrane based on anionic surfactant/UIO-66 derivative

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210553557.2A CN115105953B (en) 2022-05-20 2022-05-20 Preparation method of carbon composite nanofiltration membrane based on anionic surfactant/UIO-66 derivative

Publications (2)

Publication Number Publication Date
CN115105953A true CN115105953A (en) 2022-09-27
CN115105953B CN115105953B (en) 2023-07-25

Family

ID=83326374

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210553557.2A Active CN115105953B (en) 2022-05-20 2022-05-20 Preparation method of carbon composite nanofiltration membrane based on anionic surfactant/UIO-66 derivative

Country Status (1)

Country Link
CN (1) CN115105953B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN117547974A (en) * 2024-01-12 2024-02-13 河南师范大学 A polypiperazinamide nanofiltration membrane with high acid-base stability and preparation method thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107583469A (en) * 2017-11-01 2018-01-16 天津工业大学 The preparation method of polyamide composite nanofiltration membrane containing amino modified nano-particle
CN110523282A (en) * 2019-09-26 2019-12-03 东华大学 A kind of UiO-66 composite forward osmosis membrane and its preparation and application
CN110833769A (en) * 2019-11-20 2020-02-25 大连理工大学 A kind of layered zirconium phosphate-based molecular sieve membrane and preparation method thereof
CN111495206A (en) * 2020-05-09 2020-08-07 山东中莱新材料技术有限公司 Preparation method of high-flux pressure-resistant ultrafiltration membrane
CN113559725A (en) * 2021-08-27 2021-10-29 深圳市爱玛特科技有限公司 Preparation method of metal organic framework polyamide thin-layer nano composite membrane (UiO-66/TFN)
US11254691B1 (en) * 2021-02-22 2022-02-22 Kuwait Institute For Scientific Research Method for making metal organic frameworks and thin film nanocomposite membranes using the same

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107583469A (en) * 2017-11-01 2018-01-16 天津工业大学 The preparation method of polyamide composite nanofiltration membrane containing amino modified nano-particle
CN110523282A (en) * 2019-09-26 2019-12-03 东华大学 A kind of UiO-66 composite forward osmosis membrane and its preparation and application
CN110833769A (en) * 2019-11-20 2020-02-25 大连理工大学 A kind of layered zirconium phosphate-based molecular sieve membrane and preparation method thereof
CN111495206A (en) * 2020-05-09 2020-08-07 山东中莱新材料技术有限公司 Preparation method of high-flux pressure-resistant ultrafiltration membrane
US11254691B1 (en) * 2021-02-22 2022-02-22 Kuwait Institute For Scientific Research Method for making metal organic frameworks and thin film nanocomposite membranes using the same
CN113559725A (en) * 2021-08-27 2021-10-29 深圳市爱玛特科技有限公司 Preparation method of metal organic framework polyamide thin-layer nano composite membrane (UiO-66/TFN)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN117547974A (en) * 2024-01-12 2024-02-13 河南师范大学 A polypiperazinamide nanofiltration membrane with high acid-base stability and preparation method thereof
CN117547974B (en) * 2024-01-12 2024-04-12 河南师范大学 A polypiperazineamide nanofiltration membrane with high acid-base stability and preparation method thereof

Also Published As

Publication number Publication date
CN115105953B (en) 2023-07-25

Similar Documents

Publication Publication Date Title
CN103272491B (en) Preparation method for in situ self-assembled organic/inorganic hybrid membrane based on coordination
CN105126638B (en) A kind of preparation method of reverse diffusion primary reconstruction MOFs NF membranes
CN104801208B (en) Sodium alginate-flaky ZIF-8 hybrid composite membrane, and preparation and application thereof
CN107469633B (en) Method for preparing membrane with enhanced water flux
CN108409981A (en) A kind of preparation method of modified metal organic frame and composite nanometer filtering film
CN102824856B (en) Preparation method for generating inorganic nanoparticle hybrid membrane in situ by using self-assembly technology
CN114177782A (en) Photocatalytic MXene composite film and preparation method thereof
CN110639371B (en) A kind of preparation method of nanometer titanium dioxide blended graphene oxide loose nanofiltration membrane and its application in dye desalination
CN113648850B (en) Preparation method of MXene/reduced porous graphene oxide (r-HGO) composite membrane with high flux and high removal rate
CN114405295A (en) A kind of high-flux graphene oxide hollow fiber composite nanofiltration membrane and preparation method thereof
CN115178109A (en) Composite nanofiltration membrane based on covalent organic framework compound NCOF and preparation method thereof
CN115041027A (en) A dual regulated two-dimensional MXene composite membrane and its preparation method
CN116672897A (en) Preparation method of polyamide composite nanofiltration membrane containing polystyrene-polyacrylamide nanoparticle intermediate layer
CN102489180A (en) Preparation method for composite porous filter membrane made of high polymer/nano material
CN115105953B (en) Preparation method of carbon composite nanofiltration membrane based on anionic surfactant/UIO-66 derivative
CN108993165A (en) A kind of layered inorganic material organic solvent nanofiltration composite membrane and preparation method thereof
CN114247305B (en) A two-dimensional nano-island@graphene heterojunction self-assembled hydrophobic nanofiltration membrane and its preparation method
CN115888414A (en) High-selectivity, high-flux and high-degree ordered self-assembled mixed matrix gas separation membrane and preparation method thereof
CN113522038B (en) Preparation method and application of composite membrane for removing pollutants in water
CN111760468B (en) Polyvinylidene fluoride composite ultrafiltration membrane for catalytic reduction of p-nitrophenol and preparation method thereof
CN108079798A (en) A kind of super hydrophilic organic membrane preparation method based on nano hydrotalcite
CN114682106B (en) Preparation method of self-supporting composite nanofiltration membrane
CN110404420A (en) A composite nanofiltration membrane using vinylon water-soluble line as (sacrificial) intermediate layer and preparation method thereof
CN115845614A (en) High-performance nanofiltration membrane containing molecular sieve/GO composite material intermediate layer and preparation method thereof
CN110743379B (en) Application of mesoporous silica nano-sheet composite film in water treatment

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
GR01 Patent grant
GR01 Patent grant