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CN118543260A - A modified polyacrylonitrile microfiber oil-water separation material and preparation method thereof - Google Patents

A modified polyacrylonitrile microfiber oil-water separation material and preparation method thereof Download PDF

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CN118543260A
CN118543260A CN202410608972.2A CN202410608972A CN118543260A CN 118543260 A CN118543260 A CN 118543260A CN 202410608972 A CN202410608972 A CN 202410608972A CN 118543260 A CN118543260 A CN 118543260A
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polyacrylonitrile
microfiber
water
oil
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金文斌
夏于旻
梁源
张耀
王莹
马克
陈雨晗
夏明鑫
万海
黄铄涵
王燕萍
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Donghua University
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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
    • B01D71/40Polymers of unsaturated acids or derivatives thereof, e.g. salts, amides, imides, nitriles, anhydrides, esters
    • B01D71/42Polymers of nitriles, e.g. polyacrylonitrile
    • B01D71/421Polyacrylonitrile
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D17/00Separation of liquids, not provided for elsewhere, e.g. by thermal diffusion
    • B01D17/08Thickening liquid suspensions by filtration
    • B01D17/085Thickening liquid suspensions by filtration with membranes
    • 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
    • B01D67/0002Organic membrane manufacture
    • B01D67/0004Organic membrane manufacture by agglomeration of particles
    • B01D67/00042Organic membrane manufacture by agglomeration of particles by deposition of fibres, nanofibres or nanofibrils
    • 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
    • B01D67/0002Organic membrane manufacture
    • B01D67/0006Organic membrane manufacture by chemical reactions
    • 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
    • B01D67/0081After-treatment of organic or inorganic membranes
    • B01D67/0093Chemical modification
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/02Details relating to pores or porosity of the membranes
    • B01D2325/028Microfluidic pore structures
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/02Details relating to pores or porosity of the membranes
    • B01D2325/0281Fibril, or microfibril structures
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2325/00Details relating to properties of membranes
    • B01D2325/36Hydrophilic membranes

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
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  • Nanotechnology (AREA)
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Abstract

The invention provides a modified polyacrylonitrile microfiber oil-water separation material and a preparation method thereof, wherein the preparation method comprises the following steps: the method comprises the steps of obtaining polyacrylonitrile fiber after wet spinning and hot drawing, wherein the inside of the polyacrylonitrile fiber is provided with a fibrillating structure and is orderly arranged along the axial direction of the fiber, chopping the polyacrylonitrile fiber, putting the chopped polyacrylonitrile fiber and water into a mechanical crusher for shearing, disassembling and crushing to obtain polyacrylonitrile microfiber aqueous dispersion, and carrying out suction filtration by using a suction filtration bottle, washing by using deionized water, and drying by using an oven to obtain the polyacrylonitrile microfiber. And then carrying out amidoxime modification on the surface of the polyacrylonitrile microfiber by using hydroxylamine hydrochloride solution to increase the hydrophilicity of the polyacrylonitrile microfiber, thus obtaining the modified polyacrylonitrile microfiber. The preparation method is simple and convenient, and has industrialization potential; the polyacrylonitrile has certain chemical stability, the modified polyacrylonitrile microfiber has plasticity and certain self-supporting property, has affinity to water and has resistance to various oils and organic solvents in the presence of an oil-water mixture, can meet various oil-water separation environments and conditions, and provides an effective solution for purifying the oil-water mixture.

Description

一种改性聚丙烯腈微纤维油水分离材料及其制备方法A modified polyacrylonitrile microfiber oil-water separation material and preparation method thereof

技术领域:Technical field:

本发明属于新型材料加工制备领域,涉及一种油水分离材料的制备方法,尤其涉及一种改性聚丙烯腈微纤维油水分离材料的制备方法。The invention belongs to the field of new material processing and preparation, and relates to a method for preparing an oil-water separation material, and in particular to a method for preparing a modified polyacrylonitrile microfiber oil-water separation material.

背景技术:Background technology:

近年来,含油废水作为人类生产生活中的副产物,阻碍了可持续发展的进程,破坏了赖以生存的自然环境,对人的生命安全造成了巨大威胁。首先,含油废水未经处理或处理不完全,其中的有害物质会渗入地下与江河湖泊汇聚,从而污染人类的淡水资源;其次,含油废水的密度比水小,会覆盖在水面上隔绝氧气,导致水生植物和动物的死亡,从而污染自然环境;最后,含油废水混入灌溉水源后其中的有害物质可能会被农作物吸收,也会对人体造成巨大伤害。因此,发明一种对含油废水的高效处理方式显得尤为迫切。In recent years, oily wastewater, as a by-product of human production and life, has hindered the process of sustainable development, destroyed the natural environment on which people depend for survival, and posed a huge threat to human life and safety. First, if oily wastewater is not treated or treated incompletely, the harmful substances in it will seep into the ground and converge with rivers, lakes and reservoirs, thereby polluting human freshwater resources; secondly, the density of oily wastewater is smaller than that of water, and it will cover the water surface and isolate oxygen, causing the death of aquatic plants and animals, thereby polluting the natural environment; finally, after oily wastewater is mixed with irrigation water sources, the harmful substances in it may be absorbed by crops and cause great harm to the human body. Therefore, it is particularly urgent to invent an efficient treatment method for oily wastewater.

为解决含油废水带来的上述影响,许多的油水分离方法被开发出来,其中包括重力分离法,吸附法,膜分离法等等。重力分离法是指利用油水两相之间互不相溶且密度存在差异,使油相在水相表面聚集,从而达到分离的效果;吸附法指的是利用吸附剂将其中一相吸附从而达到分离的目的;膜分离法指的是利用各种具有特殊结构的薄膜材料,使其中一相选择性地透过,具有能耗低,操作便捷,分离效率高等优点。因此在研究油水分离方法的过程中,制备不同功能的油水分离膜成为了学者和专家们研究的重点。吉林大学薛明教授课题组在金属网上涂覆了UiO-66微纳米结构涂层并制备成膜,使得该膜具有亲水性和水下超疏油性,且油水分离效率高达99.99%,水通量最高为12.7×104L/(m2h),能够很容易地从各种油水混合物中捕获油含量小于4ppm的高纯水,并表现出了很高的稳定性和耐久性。但该膜的防污及重复利用能力和耐腐蚀能力较弱,不具有高效的去污方法,且在一些复杂的腐蚀性的油水分离环境下具有一定的局限性。Mohamed Obaid等人用静电纺丝法制备了聚偏氟乙烯(PVDF)纳米纤维毡,再用三乙醇胺(TEA)在毡表面改性修饰形成亲水微球得到改性PVDF油水分离膜。该膜同样具有超高的20664L/(m2h)的油水分离水通量和2727L/(m2h)的乳液分离水通量,分离效率效率高达99%。但静电纺丝法制备PVDF纳米纤维需要加入有机溶剂N,N-二甲基甲酰胺(DMF),从而间接危害环境和人体健康,且制备周期长,不利于大规模生产和应用。In order to solve the above-mentioned effects of oily wastewater, many oil-water separation methods have been developed, including gravity separation, adsorption, membrane separation, etc. Gravity separation refers to the use of the immiscibility of oil and water phases and the difference in density to make the oil phase aggregate on the surface of the water phase, thereby achieving the effect of separation; adsorption refers to the use of adsorbents to adsorb one of the phases to achieve the purpose of separation; membrane separation refers to the use of various thin film materials with special structures to selectively allow one of the phases to pass through, which has the advantages of low energy consumption, convenient operation, and high separation efficiency. Therefore, in the process of studying oil-water separation methods, the preparation of oil-water separation membranes with different functions has become the focus of research by scholars and experts. Professor Xue Ming's research group at Jilin University coated a UiO-66 micro-nanostructure coating on a metal mesh and prepared a membrane, making the membrane hydrophilic and underwater superoleophobic, with an oil-water separation efficiency of up to 99.99%, and a maximum water flux of 12.7×10 4 L/(m 2 h). It can easily capture high-purity water with an oil content of less than 4ppm from various oil-water mixtures, and exhibits high stability and durability. However, the membrane's antifouling, reuse and corrosion resistance are weak, it does not have an efficient decontamination method, and has certain limitations in some complex corrosive oil-water separation environments. Mohamed Obaid et al. prepared polyvinylidene fluoride (PVDF) nanofiber felt by electrospinning, and then used triethanolamine (TEA) to modify the felt surface to form hydrophilic microspheres to obtain a modified PVDF oil-water separation membrane. The membrane also has an ultra-high water flux of 20664L/(m 2 h) for oil-water separation and 2727L/(m 2 h) for emulsion separation, with a separation efficiency of up to 99%. However, the electrospinning method for preparing PVDF nanofibers requires the addition of an organic solvent, N,N-dimethylformamide (DMF), which indirectly harms the environment and human health, and the preparation cycle is long, which is not conducive to large-scale production and application.

膜分离法进行油水分离时由于其具有丰富的孔洞结构来吸收液相,使得分离效率高,分离通量大。聚丙烯腈是应用广泛的通用塑料,廉价易得,且聚丙烯腈微纤维制备简便,物理化学性质稳定,本身具有亲水的特性。经过剪切拆解将纤维制备得到聚丙烯腈微纤维后,再通过偕胺肟化改性,能够得到的具有亲水-水下超疏油的特性的改性聚丙烯腈微纤维。该改性聚丙烯腈微纤维属于亲水疏油材料,具有丰富的微观孔洞结构吸附和储存水,且制备加工操作简便,制备成本低,可多次重复利用,在大规模使用和连续化生产过程中具有明显的优势,对制备油水分离的微纤维材料具有一定的指导意义。When membrane separation is performed for oil-water separation, due to its abundant pore structure to absorb liquid phase, separation efficiency is high and separation flux is large. Polyacrylonitrile is a widely used general plastic, cheap and easy to obtain, and polyacrylonitrile microfiber is easy to prepare, and its physicochemical properties are stable, and it has hydrophilic characteristics. After shearing and disassembling, the fiber is prepared to obtain polyacrylonitrile microfibers, and then modified by amidoximation, the modified polyacrylonitrile microfibers with hydrophilic-underwater super-oleophobic characteristics that can be obtained. The modified polyacrylonitrile microfibers belong to hydrophilic oleophobic materials, with abundant microscopic pore structures to absorb and store water, and the preparation and processing are simple and easy to operate, the preparation cost is low, and it can be repeatedly reused, and there are obvious advantages in large-scale use and continuous production processes, and there is a certain guiding significance for the preparation of microfiber materials for oil-water separation.

发明内容:Summary of the invention:

本发明的目的在于制备出一种制备加工操作简便、油水分离效果显著、物理化学性质稳定、能重复循环使用、可以大规模连续化生产的微纤维油水分离材料。The purpose of the present invention is to prepare a microfiber oil-water separation material which has simple preparation and processing operation, significant oil-water separation effect, stable physical and chemical properties, can be repeatedly recycled, and can be produced on a large scale and continuously.

为了实现上述目的,本发明提供一种改性聚丙烯腈微纤维油水分离材料的制备方案:In order to achieve the above object, the present invention provides a preparation method of modified polyacrylonitrile microfiber oil-water separation material:

(1)将湿法纺丝和热牵伸后得到的聚丙烯腈纤维用裁刀进行短切,制得聚丙烯腈短切纤维,再将短切纤维放入机械粉碎机中,加入水,进行机械剪切、拆解、粉碎,得到聚丙烯腈微纤维水分散液;(1) chopping the polyacrylonitrile fibers obtained by wet spinning and hot drawing with a cutter to obtain polyacrylonitrile chopped fibers, and then placing the chopped fibers in a mechanical pulverizer, adding water, and mechanically shearing, disassembling, and pulverizing to obtain a polyacrylonitrile microfiber aqueous dispersion;

(2)将步骤(1)中得到的聚丙烯腈微纤维水分散液进行抽滤,用去离子水洗涤,再放入烘箱中烘干,得到聚丙烯腈微纤维;(2) filtering the polyacrylonitrile microfiber aqueous dispersion obtained in step (1), washing with deionized water, and drying in an oven to obtain polyacrylonitrile microfibers;

(3)将步骤(2)中得到的聚丙烯腈微纤维用盐酸羟胺溶液进行改性,增加其表面亲水性,再抽滤后用去离子水洗涤,放入烘箱中烘干,得到改性聚丙烯腈微纤维油水分离材料。(3) The polyacrylonitrile microfibers obtained in step (2) are modified with a hydroxylamine hydrochloride solution to increase their surface hydrophilicity, and then filtered and washed with deionized water, and then placed in an oven for drying to obtain a modified polyacrylonitrile microfiber oil-water separation material.

作为优选,步骤(1)中的短切纤维为1-2cm,加入的纤维和水的比例为每10g纤维加入2L水,机械剪切、拆解、粉碎时,剪切速率为105s-1,时间为10-90分钟,进一步优选为40-60分钟,最优选为50分钟。Preferably, the chopped fibers in step (1) are 1-2 cm in length, and the ratio of added fibers to water is 2 L of water per 10 g of fibers. During mechanical shearing, disassembly and pulverization, the shear rate is 10 5 s -1 , and the time is 10-90 minutes, more preferably 40-60 minutes, and most preferably 50 minutes.

作为优选,步骤(3)中的盐酸羟胺溶液浓度为2-6%,最优选为4%;聚丙烯腈微纤维质量为5-15g,最优选为10g;反应时间为1-3h,最优选为2h。Preferably, the concentration of the hydroxylamine hydrochloride solution in step (3) is 2-6%, most preferably 4%; the mass of the polyacrylonitrile microfibers is 5-15 g, most preferably 10 g; and the reaction time is 1-3 h, most preferably 2 h.

与现有技术相比,本发明具有以下积极有益效果:Compared with the prior art, the present invention has the following positive and beneficial effects:

(1)本发明利用了聚丙烯腈纤维在湿法纺丝和热牵伸的过程中,纤维内部沿纤维轴向产生的原纤化结构,将其进行剪切拆解粉碎,破坏原纤化结构间径向的弱分子间结合力,保留轴向强化学键结合力,使得原纤化结构暴露出来,并得到聚丙烯腈微纤维。该微纤维经过盐酸羟胺溶液进行偕胺肟化亲水改性,再通过抽滤使微纤维间相互穿插,交叠,支持得到改性聚丙烯腈微纤维油水分离膜。这种较为新颖的机械拆解原纤化结构制备微纤维、再通过改性提高其亲水性、最后抽滤制备微纤维油水分离膜的方法,解决了现有的油水分离材料的制备中加工操作复杂、难以重复利用、难以大规模连续化生产等问题,并且能大大降低制备的成本。(1) The present invention utilizes the fibrillated structure generated along the fiber axis inside the polyacrylonitrile fiber during the wet spinning and hot stretching process, and shears and disassembles it to break it, thereby destroying the weak radial intermolecular bonding force between the fibrillated structures and retaining the strong axial chemical bond bonding force, so that the fibrillated structure is exposed and polyacrylonitrile microfibers are obtained. The microfibers are hydrophilically modified by amidoximation with a hydroxylamine hydrochloride solution, and then the microfibers are interlaced and overlapped by suction filtration to support the obtained modified polyacrylonitrile microfiber oil-water separation membrane. This relatively novel method of mechanically disassembling the fibrillated structure to prepare microfibers, then improving their hydrophilicity by modification, and finally preparing the microfiber oil-water separation membrane by suction filtration solves the problems of complex processing operations, difficulty in reuse, and difficulty in large-scale continuous production in the preparation of existing oil-water separation materials, and can greatly reduce the cost of preparation.

(2)本发明制备改性聚丙烯腈微纤维油水分离材料的方法中,所需要的原料为聚丙烯腈纤维,材料廉价易得,且具有优异的亲水疏油性和物理化学稳定性,且制备过程中操作简便,所需化学试剂较少,对人体和环境破坏较小,制备加工过程简单安全。在拆解制备微纤维的过程中,仅仅为物理形态上的变化,而聚丙烯腈的化学结构、官能团没有被破坏,因此本身的化学稳定性和亲水性都没有丧失。(2) In the method for preparing modified polyacrylonitrile microfiber oil-water separation material of the present invention, the required raw material is polyacrylonitrile fiber, which is cheap and easy to obtain, and has excellent hydrophilicity and oleophobicity and physical and chemical stability. The preparation process is simple to operate, requires fewer chemical reagents, causes less damage to the human body and the environment, and the preparation process is simple and safe. In the process of disassembling and preparing microfibers, only the physical form changes, and the chemical structure and functional groups of polyacrylonitrile are not destroyed, so the chemical stability and hydrophilicity of the fiber itself are not lost.

(3)本发明制备的改性聚丙烯腈微纤维在微观上具有微纳米级别的孔洞,这些孔洞是由改性聚丙烯腈微纤维间相互穿插、交叠、支撑形成的,但宏观上该微纤维呈现为松散状,具有可塑性。因此该微纤维能够通过抽滤被制备为各种形状,以满足在复杂的环境或特定的设备中,以设定的形态进行油水分离(图2)。(3) The modified polyacrylonitrile microfibers prepared by the present invention have micro-nano-scale pores at the microscopic level, which are formed by the interpenetration, overlap and support between the modified polyacrylonitrile microfibers, but at the macroscopic level, the microfibers are loose and plastic. Therefore, the microfibers can be prepared into various shapes by suction filtration to meet the requirements of oil-water separation in a complex environment or specific equipment in a set form (Figure 2).

(4)本发明制备的改性聚丙烯腈微纤维油水分离材料具有微纳米级别的孔洞,能够高效地吸附并保留水相。同时,用盐酸羟胺溶液偕胺肟化改性后,该微纤维的亲水性进一步增强,并且在水下具有超疏油性(图5和6)。(4) The modified polyacrylonitrile microfiber oil-water separation material prepared by the present invention has micro-nano-scale pores, which can efficiently adsorb and retain the water phase. At the same time, after being modified by amidoximation with hydroxylamine hydrochloride solution, the hydrophilicity of the microfiber is further enhanced, and it has superoleophobicity underwater (Figures 5 and 6).

(5)改性聚丙烯腈微纤维油水分离材料的物理和化学稳定性也为其循环利用提供了保障。使用后被污染的改性聚丙烯腈微纤维油水分离膜,可以将微纤维膜充分打散于水中,使其回到松散的微纤维形态,再通过一定手段除去油污,即可重新将微纤维回收制备成微纤维膜继续用于油水分离,并且能依旧保持超高的分离效率(图8)。(5) The physical and chemical stability of modified polyacrylonitrile microfiber oil-water separation materials also provides a guarantee for their recycling. After use, the contaminated modified polyacrylonitrile microfiber oil-water separation membrane can be fully dispersed in water to return to a loose microfiber form. Then, the oil stains can be removed by certain means, and the microfibers can be recycled and prepared into microfiber membranes for continued oil-water separation, and the ultra-high separation efficiency can still be maintained (Figure 8).

附图说明:Description of the drawings:

图1是由聚丙烯腈微纤维(PNF)制备改性聚丙烯腈微纤维(AOPNF)的偕胺肟化反应的方程式。FIG. 1 is an equation for the amidoximation reaction of preparing modified polyacrylonitrile microfibers (AOPNF) from polyacrylonitrile microfibers (PNF).

图2是实例1中的聚丙烯腈和改性聚丙烯腈微纤维膜的实物图、松散状实物图和场发射扫描电子显微镜(FE-SEM)形貌图,以及改性聚丙烯腈微纤维的可塑性展示。FIG. 2 is a physical picture, a loose physical picture and a field emission scanning electron microscope (FE-SEM) morphology picture of the polyacrylonitrile and modified polyacrylonitrile microfiber membranes in Example 1, and a display of the plasticity of the modified polyacrylonitrile microfibers.

图3是实例1中的聚丙烯腈微纤维和改性聚丙烯腈微纤维的X射线光电子能谱(XPS)分析图。FIG. 3 is an X-ray photoelectron spectroscopy (XPS) analysis chart of the polyacrylonitrile microfibers and modified polyacrylonitrile microfibers in Example 1.

图4是实例1中的聚丙烯腈微纤维和改性聚丙烯腈微纤维的红外(FTIR-ATR)分析图FIG. 4 is an infrared (FTIR-ATR) analysis of polyacrylonitrile microfibers and modified polyacrylonitrile microfibers in Example 1

图5是实例1中的聚丙烯腈和改性聚丙烯腈微纤维的空气中水接触角、水下氯仿接触角和水下环己烷接触角的比较。FIG. 5 is a comparison of the water contact angle in air, the underwater chloroform contact angle, and the underwater cyclohexane contact angle of the polyacrylonitrile and modified polyacrylonitrile microfibers in Example 1.

图6是相同体积(10μL)水被实例1中的聚丙烯腈和改性聚丙烯腈微纤维膜完全吸附所需的时间。FIG. 6 shows the time required for the same volume (10 μL) of water to be completely adsorbed by the polyacrylonitrile and modified polyacrylonitrile microfiber membranes in Example 1.

图7是实例1中的改性聚丙烯腈微纤维膜阻隔油(氯仿)照片及分离环己烷(红)-水(蓝)油水混合物的过程。FIG. 7 is a photograph of the modified polyacrylonitrile microfiber membrane in Example 1 blocking oil (chloroform) and the process of separating the cyclohexane (red)-water (blue) oil-water mixture.

图8是实例1中的聚丙烯腈微纤维膜、改性聚丙烯腈微纤维膜和打散、回收、重新制备的改性聚丙烯腈微纤维膜对环己烷-水油水混合物在10个循环内的分离效率和平均分离效率。FIG8 shows the separation efficiency and average separation efficiency of the polyacrylonitrile microfiber membrane, the modified polyacrylonitrile microfiber membrane and the modified polyacrylonitrile microfiber membrane that was broken up, recovered and re-prepared for cyclohexane-water-oil-water mixture in 10 cycles in Example 1.

实例1Example 1

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为50分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L4%的盐酸羟胺溶液调节至pH为8,再加入10g聚丙烯腈微纤维后在60℃下反应2小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 50 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 4% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 10g of polyacrylonitrile microfibers were added and reacted at 60°C for 2 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为2-10μm,长度约为10-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为82°、160°和174°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了99.16%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 2-10 μm and a length of about 10-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 82°, 160° and 174° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 99.16% for cyclohexane-water mixture.

该种改性聚丙烯腈微纤维制备方法高效便捷,制备周期短,对人体健康和环境友好,利于大规模产业化制备。同时,聚丙烯腈微纤维材料因其宏观为“松散状”的特性而具有可塑性,可被抽滤为各种形状(如附图2所示)。结合聚丙烯腈本身优异的耐溶剂性,表明其能够适应不同的环境,可实现在各种实际条件下的高效油水分离。将使用过的改性聚丙烯腈微纤维膜打散后分散于水中形成水分散液,去除表面的污渍后将其重新回收抽滤成膜,再次用于环己烷-水混合物分离实验,测得其分离效率依然高达98.84%(如附图8所示)。This modified polyacrylonitrile microfiber preparation method is efficient and convenient, with a short preparation cycle, is friendly to human health and the environment, and is conducive to large-scale industrial preparation. At the same time, the polyacrylonitrile microfiber material has plasticity due to its macroscopic "loose" characteristics and can be filtered into various shapes (as shown in Figure 2). Combined with the excellent solvent resistance of polyacrylonitrile itself, it shows that it can adapt to different environments and can achieve efficient oil-water separation under various practical conditions. The used modified polyacrylonitrile microfiber membrane is broken up and dispersed in water to form an aqueous dispersion. After removing the stains on the surface, it is recovered and filtered to form a membrane, and then used again in the cyclohexane-water mixture separation experiment. The separation efficiency is still as high as 98.84% (as shown in Figure 8).

实例2Example 2

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为10分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L4%的盐酸羟胺溶液调节至pH为8,再加入10g聚丙烯腈微纤维后在60℃下反应2小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 10 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 4% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 10g of polyacrylonitrile microfibers were added and reacted at 60°C for 2 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为10-30μm,长度约为10-500μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为90°、146°和147°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了98.42%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 10-30 μm and a length of about 10-500 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 90°, 146° and 147° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 98.42% for cyclohexane-water mixture.

实例3Example 3

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为90分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L4%的盐酸羟胺溶液调节至pH为8,再加入10g聚丙烯腈微纤维后在60℃下反应2小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 90 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 4% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 10g of polyacrylonitrile microfibers were added and reacted at 60°C for 2 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为1-10μm,长度约为5-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为98°、159°和153°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了98.51%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 1-10 μm and a length of about 5-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 98°, 159° and 153° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 98.51% for cyclohexane-water mixture.

实例4Example 4

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为50分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L2%的盐酸羟胺溶液调节至pH为8,再加入10g聚丙烯腈微纤维后在60℃下反应2小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 50 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 2% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 10g of polyacrylonitrile microfibers were added and reacted at 60°C for 2 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为2-10μm,长度约为10-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为110°、148°和155°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了98.78%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 2-10 μm and a length of about 10-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 110°, 148° and 155° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 98.78% for cyclohexane-water mixture.

实例5Example 5

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为50分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L6%的盐酸羟胺溶液调节至pH为8,再加入10g聚丙烯腈微纤维后在60℃下反应2小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 50 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 6% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 10g of polyacrylonitrile microfibers were added and reacted at 60°C for 2 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为2-10μm,长度约为10-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为108°、133°和148°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了98.11%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 2-10 μm and a length of about 10-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 108°, 133° and 148° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 98.11% for cyclohexane-water mixture.

实例6Example 6

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为50分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L4%的盐酸羟胺溶液调节至pH为8,再加入5g聚丙烯腈微纤维后在60℃下反应2小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 50 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 4% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 5g of polyacrylonitrile microfibers were added and reacted at 60°C for 2 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为2-10μm,长度约为10-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为88°、153°和160°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了98.28%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 2-10 μm and a length of about 10-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 88°, 153° and 160° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 98.28% for cyclohexane-water mixture.

实例7Example 7

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为50分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L4%的盐酸羟胺溶液调节至pH为8,再加入15g聚丙烯腈微纤维后在60℃下反应2小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 50 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 4% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 15g of polyacrylonitrile microfibers were added and reacted at 60°C for 2 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为2-10μm,长度约为10-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为80°、160°和166°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了98.56%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 2-10 μm and a length of about 10-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 80°, 160° and 166° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 98.56% for cyclohexane-water mixture.

实例8Example 8

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为50分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L4%的盐酸羟胺溶液调节至pH为8,再加入10g聚丙烯腈微纤维后在60℃下反应1小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 50 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 4% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 10g of polyacrylonitrile microfibers were added and reacted at 60°C for 1 hour to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为2-10μm,长度约为10-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为82°、160°和174°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了99.16%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 2-10 μm and a length of about 10-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 82°, 160° and 174° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 99.16% for cyclohexane-water mixture.

实例9Example 9

将湿法纺丝和热牵伸得到的聚丙烯腈纤维用裁刀短切至1-2cm,得到短切纤维,将其放入机械粉碎机中,加入2L水,进行机械剪切、拆解、粉碎,时间为50分钟,剪切速率为105s-1。待剪切、拆解、粉碎结束后,将得到的聚丙烯腈微纤维水分散液抽滤除去水,用去离子水洗涤3次,再放入70℃的烘箱中干燥2小时,得到聚丙烯腈微纤维。随后用碳酸钠将1L4%的盐酸羟胺溶液调节至pH为8,再加入10g聚丙烯腈微纤维后在60℃下反应3小时得到改性聚丙烯腈微纤维油水分离材料。The polyacrylonitrile fibers obtained by wet spinning and hot drawing were cut into 1-2 cm with a cutter to obtain short-cut fibers, which were placed in a mechanical pulverizer, and 2L of water was added for mechanical shearing, disassembly, and crushing for 50 minutes at a shear rate of 10 5 s -1 . After the shearing, disassembly, and crushing were completed, the obtained polyacrylonitrile microfiber aqueous dispersion was filtered to remove water, washed with deionized water 3 times, and then placed in an oven at 70°C for 2 hours to obtain polyacrylonitrile microfibers. Subsequently, 1L of 4% hydroxylamine hydrochloride solution was adjusted to pH 8 with sodium carbonate, and then 10g of polyacrylonitrile microfibers were added and reacted at 60°C for 3 hours to obtain a modified polyacrylonitrile microfiber oil-water separation material.

该实例得到的改性聚丙烯腈微纤维油水分离材料直径约为2-10μm,长度约为10-100μm,将其抽滤成膜,测试得到空气中水接触角、水下氯仿接触角和水下环己烷接触角分别为96°、161°和153°。该改性聚丙烯腈微纤维膜亲水疏油,能阻隔氯仿,并对环己烷-水混合物的分离效率达到了98.22%。The modified polyacrylonitrile microfiber oil-water separation material obtained in this example has a diameter of about 2-10 μm and a length of about 10-100 μm. It is filtered to form a membrane, and the test results show that the water contact angle in the air, the underwater chloroform contact angle and the underwater cyclohexane contact angle are 96°, 161° and 153° respectively. The modified polyacrylonitrile microfiber membrane is hydrophilic and oleophobic, can block chloroform, and has a separation efficiency of 98.22% for cyclohexane-water mixture.

表1各个实例中各项参数和实验结果Table 1 Parameters and experimental results in each example

*绿色标注为与实例1相比较所改变的参数或条件。*Parameters or conditions marked in green are changed compared with Example 1.

Claims (6)

1. The modified polyacrylonitrile microfiber oil-water separation material and the preparation method thereof are characterized by comprising the following steps:
(1) Chopping polyacrylonitrile fibers obtained after wet spinning and hot drawing by using a cutter to obtain polyacrylonitrile chopped fibers, putting the chopped fibers into a mechanical crusher, adding water, and mechanically shearing, disassembling and crushing to obtain polyacrylonitrile microfiber aqueous dispersion;
(2) Carrying out suction filtration on the polyacrylonitrile microfiber aqueous dispersion liquid obtained in the step (1), washing with deionized water, and then putting into a drying oven for drying to obtain polyacrylonitrile microfiber;
(3) And (3) modifying the polyacrylonitrile microfiber obtained in the step (2) by using hydroxylamine hydrochloride solution to increase the surface hydrophilicity, filtering, washing by using deionized water, and drying in an oven to obtain the modified polyacrylonitrile microfiber oil-water separation material.
2. The method according to claim 1, wherein the length of the polyacrylonitrile chopped fiber in the step (1) is 1-2cm, the ratio of the mass of the polyacrylonitrile fiber added to the deionized water added in the mechanical shearing, disassembling and crushing processes is 10g of fiber to 2L of deionized water, the shearing rate is 10 5s-1, and the time is 10-90 minutes.
3. The method according to claim 1, wherein the polyacrylonitrile microfiber aqueous dispersion in step (2) is filtered in a filter flask under a vacuum pressure of 0.03MPa, washed 3 times with deionized water, and dried in an oven at 70 ℃ for 2 hours after removal.
4. The method according to claim 1, wherein the surface hydrophilic modification is carried out by using a hydroxylamine hydrochloride solution in the step (3), the concentration of the hydroxylamine hydrochloride solution is 2-6%, the amount is 1L, the amount of the polyacrylonitrile microfiber is 5-15g, the stirring rate is 200rpm, the reaction temperature is 60 ℃, the reaction time is 1-3 hours, the deionized water is 3 times, the oven temperature is 70 ℃, and the drying time is 2 hours.
5. The preparation method according to claim 1, wherein the obtained modified polyacrylonitrile microfiber has a diameter ranging from 1 to 30 μm and a length ranging from 5 to 100 μm, the modified polyacrylonitrile microfiber film prepared by suction filtration has an air water contact angle of 80 to 110 degrees, an underwater chloroform contact angle of 130 to 160 degrees, an underwater cyclohexane contact angle of 145 to 175 degrees, and a cyclohexane/water mixture separation efficiency of 98.1 to 99.2%.
6. A modified polyacrylonitrile microfiber oil-water separation material, characterized by being prepared from the experimental parameters according to any one of claims 1 to 5.
CN202410608972.2A 2024-05-16 2024-05-16 A modified polyacrylonitrile microfiber oil-water separation material and preparation method thereof Pending CN118543260A (en)

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CN106861435A (en) * 2017-01-16 2017-06-20 湖北大学 A kind of preparation method of the polyacrylonitrile bionic thin film for for oil hydrosol separate
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