CN104674382B - Preparation method of porous carbon nanofiber for capacitive deionization - Google Patents

Preparation method of porous carbon nanofiber for capacitive deionization Download PDF

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CN104674382B
CN104674382B CN201510063832.2A CN201510063832A CN104674382B CN 104674382 B CN104674382 B CN 104674382B CN 201510063832 A CN201510063832 A CN 201510063832A CN 104674382 B CN104674382 B CN 104674382B
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porous carbon
capacitive deionization
nanofibers
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capacitor
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CN104674382A (en
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刘建允
王世平
熊祝标
程健
安乐
杨健茂
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Donghua University
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Abstract

本发明涉及一种电容去离子用多孔碳纳米纤维的制备方法,包括:(1)将碳前驱体、有机造孔剂、过渡金属盐溶解于溶剂中,得到纺丝溶液;(2)将上述纺丝溶液进行静电纺丝,得到复合纳米纤维,然后依次进行预氧化、炭化、酸洗处理,即得多孔碳纳米纤维。本发明制备出的碳纳米纤维富含介孔、微孔结构,比表面积高、柔韧性好、电阻小、浸润性好,在形成双电层的性能上表现优异,非常适用于组装电容器并用于脱盐。

The invention relates to a preparation method of porous carbon nanofibers for capacitive deionization, comprising: (1) dissolving a carbon precursor, an organic pore-forming agent, and a transition metal salt in a solvent to obtain a spinning solution; (2) dissolving the above-mentioned Electrospinning is performed on the spinning solution to obtain composite nanofibers, which are then pre-oxidized, carbonized and pickled sequentially to obtain porous carbon nanofibers. The carbon nanofibers prepared by the present invention are rich in mesoporous and microporous structures, have high specific surface area, good flexibility, low resistance, good wettability, excellent performance in forming electric double layers, and are very suitable for assembling capacitors and for desalination.

Description

一种电容去离子用多孔碳纳米纤维的制备方法A preparation method of porous carbon nanofibers for capacitive deionization

技术领域technical field

本发明属于纳米纤维领域,特别涉及一种电容去离子用多孔碳纳米纤维的制备方法。The invention belongs to the field of nanofibers, in particular to a method for preparing porous carbon nanofibers for capacitive deionization.

背景技术Background technique

众所周知,水是生命之源,而淡水资源全球性匮乏是制约众多国家经济发展的关键因素,更是与人们的日常生活密切相关。苦咸水含量丰富,是解决淡水资源短缺的重要水源。迄今为止,人们已经开发了蒸馏法、电渗析、反渗透、活性炭吸附、离子交换法等多种去离子技术用于苦咸水淡化。但是蒸馏法、反渗透属于高耗能工艺,电渗析过程会由于电解作用产生气体,存在安全隐患;活性炭吸附剂、膜、离子交换树脂再生过程费用昂贵,且可能造成二次污染。淡水资源紧缺的现状迫使我们尽快开发一种高效率、低能耗、无污染、再生简单、安全的理想工艺。As we all know, water is the source of life, and the global scarcity of fresh water resources is a key factor restricting the economic development of many countries, and it is closely related to people's daily life. Brackish water is rich in content and is an important water source to solve the shortage of fresh water resources. So far, people have developed a variety of deionization technologies such as distillation, electrodialysis, reverse osmosis, activated carbon adsorption, and ion exchange for desalination of brackish water. However, distillation and reverse osmosis are energy-intensive processes. The electrodialysis process will generate gas due to electrolysis, which has potential safety hazards. The regeneration process of activated carbon adsorbents, membranes, and ion exchange resins is expensive and may cause secondary pollution. The shortage of fresh water resources forces us to develop an ideal process with high efficiency, low energy consumption, no pollution, simple regeneration and safety as soon as possible.

电容器(Capacitors)是近几十年来,国内外发展起来的一种新型储能元件,具有可以大电流充放电,充放电效率高,性能循环稳定性好,比功率高、无污染等优点。因此,超级电容器是一种高效、实用、环保、低成本的能量存储装置,它同时又是一种新型节能的含盐水淡化装置。采用比表面积较大的多孔材料作为电极,利用双电层电容吸附溶液中的离子从而达到含盐水中离子去除的目的。Capacitors are a new type of energy storage element developed at home and abroad in recent decades. They have the advantages of high current charge and discharge, high charge and discharge efficiency, good performance cycle stability, high specific power, and no pollution. Therefore, the supercapacitor is an efficient, practical, environmentally friendly, and low-cost energy storage device, and it is also a new type of energy-saving brine desalination device. Porous materials with a large specific surface area are used as electrodes, and the electric double layer capacitance is used to adsorb ions in the solution so as to achieve the purpose of removing ions in the brine.

目前电容脱盐的研究热点主要集中于开发高比能量、高比功率的电极材料,碳素材料由于具有高比表面积和良好的双电层电容性能是常用的电极材料。碳素材料研究主要集中在具有高比表面积和内阻较小的多孔碳材料和对碳基材料进行改性研究等方面。常用的碳材料有活性炭、碳纳米管、碳气凝胶、碳黑、碳纳米纤维等。在众多的碳素材料中活性炭、碳纳米管和碳气凝胶被认为是前景较好的新型碳材料。At present, the research hotspots of capacitive desalination mainly focus on the development of electrode materials with high specific energy and high specific power. Carbon materials are commonly used electrode materials due to their high specific surface area and good electric double layer capacitance performance. Research on carbon materials mainly focuses on porous carbon materials with high specific surface area and low internal resistance, and research on the modification of carbon-based materials. Commonly used carbon materials include activated carbon, carbon nanotubes, carbon aerogels, carbon black, and carbon nanofibers. Among numerous carbon materials, activated carbon, carbon nanotubes and carbon aerogels are considered to be promising new carbon materials.

活性炭虽然具有较大的比表面积,但是其微孔居多(孔径<2nm),对双电层的贡献较小,很多水合离子较难可逆地进、出微孔,电容去离子效率低。而碳纳米管较难均匀分散,而且改性修饰后存在一定的缺陷,限制了碳纳米管的进一步应用。碳气凝胶导电性好,具有较多的介孔结构,有利于离子的传输和扩散,是超级电容器较理想的电极材料,但是制备成本较高,且不易于进行大规模生产。Although activated carbon has a large specific surface area, its micropores are mostly (pore diameter <2nm), which contributes little to the electric double layer. It is difficult for many hydrated ions to reversibly enter and exit the micropores, and the capacitive deionization efficiency is low. However, carbon nanotubes are difficult to disperse uniformly, and there are certain defects after modification, which limits the further application of carbon nanotubes. Carbon airgel has good electrical conductivity and more mesoporous structure, which is conducive to the transmission and diffusion of ions. It is an ideal electrode material for supercapacitors, but the preparation cost is high and it is not easy to mass-produce.

静电纺丝技术是制备纳米纤维(直径范围为50-500nm)最简单、有效的理想方法,所制备的纳米纤维比表面积高、纤维直径均匀,较适合用于制备碳纳米纤维材料。但所得碳纳米纤维的孔隙率相对较低,需要物理活化(CO2活化、水蒸气活化)或化学活化(ZnCl2活化、KOH活化等),因此开发简单的高介孔、微孔率碳纳米纤维的制备方法仍是提高电容去离子性能的关键。Electrospinning technology is the simplest and most effective ideal method for preparing nanofibers (diameter range of 50-500nm). The prepared nanofibers have high specific surface area and uniform fiber diameter, which are more suitable for preparing carbon nanofiber materials. However, the porosity of the resulting carbon nanofibers is relatively low, requiring physical activation ( CO2 activation, water vapor activation) or chemical activation (ZnCl2 activation, KOH activation, etc.), so the development of simple high mesoporous, microporous carbon nanofibers The preparation method of the fiber is still the key to improve the capacitive deionization performance.

发明内容Contents of the invention

本发明所要解决的技术问题是提供一种电容去离子用多孔碳纳米纤维的制备方法,该方法制备出的碳纳米纤维富含介孔、微孔结构,比表面积高、柔韧性好、电阻小、浸润性好,在形成双电层的性能上表现优异,非常适用于组装电容器并用于脱盐。The technical problem to be solved by the present invention is to provide a method for preparing porous carbon nanofibers for capacitive deionization. The carbon nanofibers prepared by this method are rich in mesopores and microporous structures, have high specific surface area, good flexibility and low resistance. , Good wettability, excellent performance in forming electric double layer, very suitable for assembling capacitors and desalination.

本发明的一种电容去离子用多孔碳纳米纤维的制备方法,包括:A method for preparing porous carbon nanofibers for capacitive deionization of the present invention, comprising:

(1)将碳前驱体、有机造孔剂、过渡金属盐溶解于溶剂中,得到纺丝溶液;其中,碳前驱体的质量分数为5-20%,有机造孔剂的质量分数为1-20%,过渡金属盐的质量分数为0-10%;(1) Dissolving the carbon precursor, organic pore-forming agent, and transition metal salt in a solvent to obtain a spinning solution; wherein, the mass fraction of the carbon precursor is 5-20%, and the mass fraction of the organic pore-forming agent is 1-20%. 20%, the mass fraction of transition metal salt is 0-10%;

(2)将上述纺丝溶液进行静电纺丝,得到复合纳米纤维,然后依次进行预氧化、炭化、酸洗处理,即得多孔碳纳米纤维。(2) Electrospinning the above spinning solution to obtain composite nanofibers, followed by pre-oxidation, carbonization and pickling in sequence to obtain porous carbon nanofibers.

所述步骤(1)中的碳前驱体为聚丙烯腈PAN、聚苯并咪唑PBI、丙烯腈与苯乙烯共聚物、丙烯腈与丙烯酸甲酯类的二元共聚物中的一种或几种。The carbon precursor in the step (1) is one or more of polyacrylonitrile PAN, polybenzimidazole PBI, acrylonitrile and styrene copolymer, acrylonitrile and methyl acrylate binary copolymer .

所述步骤(1)中的有机造孔剂为聚甲基丙烯酸甲酯PMMA、聚乳酸PLA、聚苯乙烯PS中的一种或几种。The organic pore-forming agent in the step (1) is one or more of polymethyl methacrylate PMMA, polylactic acid PLA, and polystyrene PS.

所述步骤(1)中的过渡金属盐为锌、铁、镍、铜、锰的卤化物、醋酸盐、磷酸盐、硫酸盐中的一种或几种。The transition metal salt in the step (1) is one or more of halides, acetates, phosphates, and sulfates of zinc, iron, nickel, copper, and manganese.

所述步骤(1)中的溶剂为N,N-二甲基甲酰胺DMF、N,N-二甲基乙酰胺DMAC中的一种或几种。The solvent in the step (1) is one or more of N,N-dimethylformamide DMF and N,N-dimethylacetamide DMAC.

所述步骤(2)中的静电纺丝工艺参数为:纺丝电压为10-25kV、接收距离为10-25cm、纺丝液推流速度为0.2-2ml/h,湿度控制在30-50%。The electrospinning process parameters in the step (2) are: the spinning voltage is 10-25kV, the receiving distance is 10-25cm, the flow rate of spinning solution is 0.2-2ml/h, and the humidity is controlled at 30-50%. .

所述步骤(2)中的预氧化为:在空气气氛中以0.5-2℃/min升温到240-280℃,并维持90-120min后,炉内冷却至室温;炭化为:在氮气或氩气气氛下,以2-10℃/min速率升温到700-1000℃,并维持90-120min后,氮气或氩气气氛下炉内冷却至室温;酸洗为:在酸溶液中浸泡8-24h,用纯水冲洗纳米纤维去除纤维表面的过渡金属盐。The pre-oxidation in the step (2) is as follows: in an air atmosphere, the temperature is raised to 240-280°C at 0.5-2°C/min, and after maintaining for 90-120min, the furnace is cooled to room temperature; carbonization is: in nitrogen or argon Under air atmosphere, heat up to 700-1000°C at a rate of 2-10°C/min, and maintain for 90-120min, then cool to room temperature in the furnace under nitrogen or argon atmosphere; pickling: soak in acid solution for 8-24h , rinse the nanofibers with pure water to remove the transition metal salts on the surface of the fibers.

所述酸为盐酸、硝酸、硫酸、磷酸中的一种或几种。The acid is one or more of hydrochloric acid, nitric acid, sulfuric acid and phosphoric acid.

所述步骤(2)得到的多孔碳纳米纤维作为自支撑电极用于组装电容器,具体为:电容器中含有1个或多个由两片大小对称的多孔碳纳米纤维组成的电极对,最外侧的电极与集流体接触并接入直流电源;同一电极对的两电极之间插入塑料网隔开作为流体通道;相邻电极对的电极之间夹入惰性导电板阻止两侧带不同电荷的离子交换;所有电极对串联接入直流电源,全部流体通道并联接入进、出水口。The porous carbon nanofiber obtained in the step (2) is used as a self-supporting electrode for assembling a capacitor, specifically: the capacitor contains one or more electrode pairs composed of two symmetrically sized porous carbon nanofibers, the outermost The electrodes are in contact with the current collector and connected to a DC power supply; a plastic mesh is inserted between the two electrodes of the same electrode pair to separate them as a fluid channel; an inert conductive plate is inserted between the electrodes of the adjacent electrode pair to prevent ion exchange with different charges on both sides ; All electrode pairs are connected in series to the DC power supply, and all fluid channels are connected in parallel to the inlet and outlet.

所述集流体为钛网、钛片、石墨片、导电石墨纸、不锈钢片、铜片、导电碳布中的一种或几种;所述惰性导电板为钛片、石墨片、导电石墨纸、不锈钢片、铜片中的一种或几种。The current collector is one or more of titanium mesh, titanium sheet, graphite sheet, conductive graphite paper, stainless steel sheet, copper sheet, conductive carbon cloth; the inert conductive plate is titanium sheet, graphite sheet, conductive graphite paper , stainless steel sheet, copper sheet or one or more.

所述电容器应用于含盐水淡化系统;其中,含盐水淡化系统包括贮水池、智能控制恒流泵、电容器、直流电源、系统控制、电导率仪、浓缩池。The capacitor is applied to a salt water desalination system; wherein, the salt water desalination system includes a water storage tank, an intelligent control constant current pump, a capacitor, a DC power supply, a system control, a conductivity meter, and a concentration pool.

所述直流电源,可控制电容器的充、放电过程。The DC power supply can control the charging and discharging process of the capacitor.

所述电导率仪能够实时监测、记录出水水质情况。The conductivity meter can monitor and record the quality of effluent water in real time.

所述恒流泵用于控制水的流速,并能根据充放电信号自动进行开关控制。The constant flow pump is used to control the flow rate of water, and can automatically switch on and off according to the charging and discharging signals.

采用制备的多孔碳纳米纤维作为自支撑电极组装含自支撑电极对的电容器脱盐装置,方法如下:Using the prepared porous carbon nanofibers as self-supporting electrodes to assemble a capacitor desalination device containing self-supporting electrode pairs, the method is as follows:

如图2所示,多孔自支撑单电极对电容器(下简称:单电极对电容器)两电极材料之间用塑料网隔开作为流体通道,两电极通过集流体接入直流电源的正、负极,超级电容器用亚格力板和硅胶垫密封、固定。As shown in Figure 2, the porous self-supporting single-electrode pair capacitor (hereinafter referred to as: single-electrode pair capacitor) is separated by a plastic mesh as a fluid channel between the two electrode materials, and the two electrodes are connected to the positive and negative poles of the DC power supply through the current collector. The supercapacitor is sealed and fixed with an acrylic plate and a silicone gasket.

如图3所示,多孔自支撑多电极对超级电容器(下简称:多电极对电容器)中同一电极对的两电极之间插入塑料网隔开作为流体通道;两侧电极通过集流体接入直流电源的正、负极;相邻电极对的电极材料之间夹入惰性导电板阻止两侧带不同电荷的离子交换,并保证电流通路。超级电容器用亚格力板和硅胶垫密封、固定;各个电极对串联接入直流电源,流体通道并联接入进、出水口。As shown in Figure 3, in a porous self-supporting multi-electrode pair supercapacitor (hereinafter referred to as multi-electrode pair capacitor), a plastic mesh is inserted between the two electrodes of the same electrode pair to separate them as a fluid channel; the electrodes on both sides are connected to DC through the current collector. The positive and negative poles of the power supply; an inert conductive plate is sandwiched between the electrode materials of adjacent electrode pairs to prevent the exchange of ions with different charges on both sides and ensure the current path. The supercapacitor is sealed and fixed with an acrylic plate and a silicone pad; each electrode pair is connected to a DC power supply in series, and the fluid channel is connected to the inlet and outlet in parallel.

本发明还组装一种单电极对电容器用于含盐水中离子去除的测试系统。如图4所示,采用一个如图2的单电极对电容器,电容器的进、出水孔通过接入恒流泵和贮水池进行溶液循环;电容器的两个电极接入恒流电源,控制电容器的充电和自放电过程,实现含盐水中离子的吸、脱附,电导率仪实时监测溶液水质状况。The invention also assembles a single-electrode pair capacitor test system for ion removal in salt water. As shown in Figure 4, a single-electrode pair capacitor as shown in Figure 2 is used, and the water inlet and outlet holes of the capacitor are connected to a constant current pump and a water storage tank for solution circulation; the two electrodes of the capacitor are connected to a constant current power supply to control the capacitor During the charging and self-discharging process, the adsorption and desorption of ions in the brine is realized, and the conductivity meter monitors the water quality of the solution in real time.

本发明还组装一种多电极对超级电容器组用于含盐水中离子去除的应用系统。如图5所示,采用多个如图3所示的多电极对电容器,电容器之间通过串联、并联、混联方式组成电容器组接入进、出水口,电容器组按串联、并联、混联方式形式接入直流电源正、负极;电容器的进、出水口通过接入双通路自控制恒流泵和贮水池、浓缩池连接进行净化水的流动和浓缩液的循环;电导率仪实时监测溶液水质状况,保证系统正常运行。The invention also assembles an application system for removing ions in salt water by assembling a multi-electrode pair supercapacitor bank. As shown in Figure 5, multiple multi-electrode pair capacitors as shown in Figure 3 are used. The capacitors are connected in series, parallel, and mixed to form a capacitor bank connected to the water inlet and outlet. The capacitor bank is connected in series, parallel, and mixed. The mode is connected to the positive and negative poles of the DC power supply; the water inlet and outlet of the capacitor are connected to the dual-channel self-control constant-flow pump and the water storage tank and the concentration tank to carry out the flow of purified water and the circulation of the concentrate; the conductivity meter monitors the solution in real time Water quality conditions to ensure the normal operation of the system.

有益效果Beneficial effect

(1)本发明采用碳前驱体、有机造孔剂、过渡金属盐复合制备出的碳纳米纤维富含介孔、微孔结构,由于过渡金属化合物可以调节有机造孔剂如PMMA或PS与PAN的相分离程度,因此可以通过有效控制使得到的纳米纤维孔结构均匀,比表面积高、柔韧性好、电阻小、浸润性好,在形成双电层的性能上表现优异,非常适用于组装电容器并用于脱盐;(1) The present invention adopts carbon precursor, organic pore forming agent, the carbon nanofiber prepared by compounding of transition metal salt is rich in mesopore, microporous structure, because transition metal compound can adjust organic pore forming agent such as PMMA or PS and PAN The degree of phase separation, so the obtained nanofiber pore structure can be effectively controlled, with high specific surface area, good flexibility, low resistance, good wettability, and excellent performance in forming an electric double layer, which is very suitable for assembling capacitors and for desalination;

(2)本发明中以自支撑多孔碳纳米纤维电极组装超级电容器,组装简单、成本低廉、运行寿命长,适用于进行苦咸水的淡化处理,具有较好的市场应用前景。(2) In the present invention, self-supporting porous carbon nanofiber electrodes are used to assemble a supercapacitor, which is simple to assemble, low in cost, and has a long operating life. It is suitable for desalination of brackish water and has a good market application prospect.

附图说明Description of drawings

图1为本发明制备的多孔碳纳米纤维SEM图,静电纺纳米纤维配方为(a)PAN:PMMA:Zn(Ac)2=4:1:1,(b)PAN:PMMA=4:1;(c)PAN:PS:ZnCl2=8:2:1,(d)PAN:PS=8:2;插图为多孔碳纳米纤维丝的截面形貌;Fig. 1 is the SEM figure of the porous carbon nanofiber prepared by the present invention, and the electrospinning nanofiber formula is (a) PAN:PMMA:Zn(Ac) 2 =4:1:1, (b) PAN:PMMA=4:1; (c) PAN:PS:ZnCl 2 =8:2:1, (d) PAN:PS=8:2; the illustration shows the cross-sectional morphology of porous carbon nanofibers;

图2为单电极对超级电容器;Figure 2 is a single-electrode pair supercapacitor;

图3为多电极对超级电容器;Figure 3 is a multi-electrode pair supercapacitor;

图4为单电极对电容器去离子测试系统;其中1为贮水池;2为恒流泵;3为单电极超级电容器;4为直流电源;5为系统控制;6为电导率仪;Figure 4 is a single-electrode pair capacitor deionization test system; wherein 1 is a water storage tank; 2 is a constant current pump; 3 is a single-electrode supercapacitor; 4 is a DC power supply; 5 is a system control; 6 is a conductivity meter;

图5为多电极对电容器组去离子应用系统;其中1为贮水池;2为智能控制恒流泵;3为多电极超级电容器组;4为直流电源;5为系统控制;6为电导率仪;7为浓缩池;Figure 5 is a multi-electrode pair capacitor bank deionization application system; 1 is a water storage tank; 2 is an intelligent control constant current pump; 3 is a multi-electrode super capacitor bank; 4 is a DC power supply; 5 is a system control; 6 is a conductivity meter ; 7 is the concentration pool;

图6为电容器的充、放电循环中电压-电流变化曲线;Fig. 6 is the voltage-current variation curve in the charging and discharging cycle of the capacitor;

图7为PAN/PMMA/Zn(Ac)2电容器充放电循环中NaCl溶液电导率的变化曲线图;Fig. 7 is PAN/PMMA/Zn(Ac) 2The change curve diagram of NaCl solution conductivity in the charge-discharge cycle of capacitor;

图8为PAN/PMMA电容器充放电循环中NaCl溶液电导率的变化曲线图;Fig. 8 is the change curve diagram of NaCl solution conductivity in PAN/PMMA capacitor charge-discharge cycle;

图9为PAN/PS/ZnCl2电容器充放电循环中NaCl溶液电导率的变化曲线图;Fig. 9 is PAN/PS/ZnClThe change curve of NaCl solution conductivity in the charge-discharge cycle of capacitor;

图10为PAN/PS电容器充放电循环中NaCl溶液电导率的变化曲线图。Fig. 10 is a curve diagram of the change of conductivity of NaCl solution in the charging and discharging cycle of PAN/PS capacitor.

具体实施方式detailed description

下面结合具体实施例,进一步阐述本发明。应理解,这些实施例仅用于说明本发明而不用于限制本发明的范围。此外应理解,在阅读了本发明讲授的内容之后,本领域技术人员可以对本发明作各种改动或修改,这些等价形式同样落于本申请所附权利要求书所限定的范围。Below in conjunction with specific embodiment, further illustrate the present invention. It should be understood that these examples are only used to illustrate the present invention and are not intended to limit the scope of the present invention. In addition, it should be understood that after reading the teachings of the present invention, those skilled in the art can make various changes or modifications to the present invention, and these equivalent forms also fall within the scope defined by the appended claims of the present application.

实施例1Example 1

以PAN为碳前驱体,聚甲基丙稀酸甲酯(PMMA)为造孔剂,调节PAN、PMMA与Zn(Ac)2的质量比为4:1:1,配制总质量分数12%的纺丝溶液,移入注射器中,设置静电纺丝电压为15kV、纺丝距离为15cm、纺丝液喷射速度为0.5ml/min,湿度控制在35%左右,静电纺丝制备PAN/PMMA/Zn(Ac)2纤维原丝。将纤维原丝置于空气气氛下进行预氧化,控制程序升温,以1℃/min升至260℃,并在260℃维持90min后自然冷却。在氮气气氛下进行碳化处理,以5℃/min升温至800℃,维持90min,冷却。在0.5M的盐酸中浸泡24h,纯水冲洗去除纤维表面的过渡金属盐。由于PAN、PMMA二者的不相容性,在纺丝过程中形成相分离,Zn(Ac)2可以调节两者的相分离状态,热处理过程后PMMA分解消失且Zn(Ac)2具有催化、活化作用,酸洗处理后即得多孔碳纳米纤维,如图1-a所示,其比表面积为468.0m2/g。将处理过的纤维剪成5cm×6cm大小的电极,放入500ppm的NaCl溶液中浸泡24h,即可按图2所示作为自支撑电极组装超级电容器器件。将超级电容器与直流电源、恒流泵、电导率仪、贮水池,按图4所示组装成去离子测试系统。电容器的进、出水口通过接入恒流泵和贮水池进行溶液循环,测试前贮水池内为500ppm的NaCl溶液;电容器的两片电极通过集流体接入恒流电源,以图6模式控制电容器的充、放电循环,实现含盐水中离子的吸、脱附。图7为充放电循环中NaCl溶液中电导率的变化曲线。其平均单循环脱盐量为脱盐量为24.5mg/g。Using PAN as the carbon precursor, polymethyl methacrylate (PMMA) as the pore-forming agent, adjusting the mass ratio of PAN, PMMA and Zn(Ac) 2 to 4:1:1, and preparing a total mass fraction of 12% The spinning solution is moved into the syringe, the electrospinning voltage is set to be 15kV, the spinning distance is 15cm, the spinning solution injection speed is 0.5ml/min, and the humidity is controlled at about 35%, and the electrospinning preparation PAN/PMMA/Zn( Ac) 2 fiber precursors. The fiber precursors were pre-oxidized in an air atmosphere, the temperature was programmed to rise to 260°C at 1°C/min, and maintained at 260°C for 90 minutes, then cooled naturally. Carry out carbonization treatment under nitrogen atmosphere, raise the temperature to 800°C at 5°C/min, maintain for 90min, and cool down. Soak in 0.5M hydrochloric acid for 24 hours, rinse with pure water to remove transition metal salts on the fiber surface. Due to the incompatibility of PAN and PMMA, phase separation is formed during the spinning process. Zn(Ac) 2 can adjust the phase separation state of the two. After the heat treatment process, PMMA decomposes and disappears, and Zn(Ac) 2 has catalytic, Activation, after pickling treatment, porous carbon nanofibers are obtained, as shown in Figure 1-a, with a specific surface area of 468.0m 2 /g. Cut the treated fibers into electrodes with a size of 5 cm × 6 cm, soak them in 500 ppm NaCl solution for 24 hours, and then assemble supercapacitor devices as self-supporting electrodes as shown in Figure 2. Assemble the supercapacitor, DC power supply, constant current pump, conductivity meter, and water storage tank as shown in Figure 4 into a deionization test system. The water inlet and outlet of the capacitor are connected to a constant current pump and a water storage tank for solution circulation. Before the test, the water storage tank is 500ppm NaCl solution; the two electrodes of the capacitor are connected to the constant current power supply through the current collector, and the capacitor is controlled in the mode shown in Figure 6 The charging and discharging cycle realizes the adsorption and desorption of ions in salt water. Fig. 7 is the change curve of the conductivity in the NaCl solution during the charge-discharge cycle. Its average single-cycle desalination capacity is 24.5mg/g.

对比例1Comparative example 1

以PAN为碳前驱体,聚甲基丙稀酸甲酯(PMMA)为造孔剂,调节PAN、PMMA的质量比为4:1,配制总质量分数10%的DMF纺丝溶液,溶液移入注射器中,设置静电纺丝电压为15kV、纺丝距离为15cm、纺丝液喷射速度为1ml/min,湿度控制在35%以下,静电纺丝制备PAN/PMMA复合纳米纤维材料,纳米纤维置于空气气氛下进行预氧化,控制程序升温,以1℃/min升温速率升至260℃,并在260℃维持90min后自然冷却。在氮气气氛下进行碳化处理,以5℃/min升温至800℃,维持90min,冷却。由于PAN、PMMA二者的不相容性,在纺丝过程中形成相分离,热处理后PMMA分解消失即得多孔碳纳米纤维,如图1-b,但是,由于不含过渡金属盐对PAN与PMMA相分离的调节,出现了很多孔径相对较大、且分布不均的孔,此外微孔含量降低,所以其比表面积为275.8m2/g。将多孔碳纳米纤维剪成5cm×6cm大小的电极,放入500ppm的NaCl溶液中浸泡24h,即可按图2所示作为自支撑电极组装电容器。将电容器与直流电源、恒流泵、电导率仪、贮水池,按图4所示组装成电容器除盐系统。电容器的进、出水口通过接入恒流泵和贮水池进行溶液循环,测试前贮水池内为500ppm的NaCl溶液;电容器的两个电极通过集流体接入恒流电源,以图6模式控制电容器的充放电循环,实现含盐水中离子的吸、脱附。图8为充放电循环中NaCl溶液中电导率的变化曲线。由于比表面积相对较低,孔径分布相对不很均匀,因此其平均单循环脱盐量为脱盐量大大降低,仅仅能够达到5.6mg/g的水平。With PAN as the carbon precursor, polymethyl methacrylate (PMMA) as the pore-forming agent, adjust the mass ratio of PAN and PMMA to be 4:1, prepare a DMF spinning solution with a total mass fraction of 10%, and transfer the solution into a syringe In the process, the electrospinning voltage is set to 15kV, the spinning distance is 15cm, the spinning liquid injection speed is 1ml/min, and the humidity is controlled below 35%. The PAN/PMMA composite nanofiber material is prepared by electrospinning, and the nanofiber is placed in the air. Pre-oxidation was carried out under the atmosphere, and the temperature was programmed to rise to 260°C at a rate of 1°C/min, and then cooled naturally at 260°C for 90 minutes. Carry out carbonization treatment under nitrogen atmosphere, raise the temperature to 800°C at 5°C/min, maintain for 90min, and cool down. Due to the incompatibility between PAN and PMMA, phase separation is formed during the spinning process. After heat treatment, PMMA decomposes and disappears to form porous carbon nanofibers, as shown in Figure 1-b. However, due to the lack of transition metal salts, PAN and The regulation of phase separation of PMMA resulted in many pores with relatively large pore size and uneven distribution. In addition, the content of micropores decreased, so its specific surface area was 275.8m 2 /g. Cut the porous carbon nanofibers into electrodes with a size of 5cm×6cm, soak them in 500ppm NaCl solution for 24 hours, and assemble capacitors as self-supporting electrodes as shown in Figure 2. Assemble the capacitor, DC power supply, constant current pump, conductivity meter, and water storage tank as shown in Figure 4 into a capacitor desalination system. The water inlet and outlet of the capacitor are connected to a constant current pump and a water storage tank for solution circulation. Before the test, the water storage tank is 500ppm NaCl solution; the two electrodes of the capacitor are connected to the constant current power supply through the current collector, and the capacitor is controlled in the mode shown in Figure 6 The charge-discharge cycle realizes the adsorption and desorption of ions in salt water. Fig. 8 is the change curve of the conductivity in the NaCl solution during the charge-discharge cycle. Due to the relatively low specific surface area and relatively uneven pore size distribution, the average single-cycle desalination capacity is greatly reduced and can only reach the level of 5.6mg/g.

实施例2Example 2

以PAN为碳前驱体,聚苯乙烯(PS)为造孔剂,调节PAN、PS与ZnCl2的质量比为8:2:1,配制总质量分数11%的纺丝溶液,移入注射器中,设置静电纺丝电压为12kV、纺丝距离为15cm、纺丝液喷射速度为0.5ml/min,湿度控制在30%左右,静电纺丝制备PAN/PS/ZnCl2纤维原丝。将纤维原丝置于空气气氛下进行预氧化,控制程序升温,以1℃/min升至250℃,并在250℃维持100min后自然冷却。在氮气气氛下进行碳化处理,以5℃/min升温至800℃,维持120min,冷却。在0.5M的盐酸中浸泡18h,纯水冲洗去除纤维表面的过渡金属盐。由于PAN、PS二者的不相溶性,在纺丝过程中形成相分离,ZnCl2可以调节两者的相分离状态,热处理过程后PS分解消失且ZnCl2具有催化、活化作用,酸洗处理后即得多孔碳纳米纤维,如图1-c,其比表面积为400.7m2/g。将处理过的纤维剪成5cm×6cm大小的电极,放入500ppm的NaCl溶液中浸泡24h,即可按图2所示作为自支撑电极组装超级电容器器件。将超级电容器与直流电源、恒流泵、电导率仪、贮水池,按图4所示组装成去离子测试系统。电容器的进、出水口通过接入恒流泵和贮水池进行溶液循环,测试前贮水池内为500ppm的NaCl溶液。电容器的两片电极通过集流体接入恒流电源,以图6模式控制电容器的充、放电循环,实现含盐水中离子的吸、脱附。图9为充放电循环中NaCl溶液中电导率的变化曲线。其平均单循环脱盐量为21.8mg/g。Using PAN as a carbon precursor, polystyrene (PS) as a pore-forming agent, adjusting the mass ratio of PAN, PS and ZnCl to 8: 2 :1, preparing a spinning solution with a total mass fraction of 11%, and moving it into a syringe, Set the electrospinning voltage to 12kV, the spinning distance to 15cm, the spinning solution injection speed to 0.5ml/min, and the humidity to be controlled at about 30%, to prepare PAN/PS/ ZnCl2 fiber precursors by electrospinning. The fiber precursors were pre-oxidized in an air atmosphere, and the temperature was programmed to increase at a rate of 1 °C/min to 250 °C, and maintained at 250 °C for 100 min and then cooled naturally. Carry out carbonization treatment under nitrogen atmosphere, raise the temperature to 800°C at 5°C/min, maintain for 120min, and cool down. Soak in 0.5M hydrochloric acid for 18 hours, rinse with pure water to remove transition metal salts on the fiber surface. Due to the incompatibility of PAN and PS, phase separation is formed during the spinning process. ZnCl 2 can adjust the phase separation state of the two. After heat treatment, PS decomposes and disappears, and ZnCl 2 has catalytic and activation functions. That is, porous carbon nanofibers, as shown in Figure 1-c, have a specific surface area of 400.7m 2 /g. Cut the treated fibers into electrodes with a size of 5 cm × 6 cm, soak them in 500 ppm NaCl solution for 24 hours, and then assemble supercapacitor devices as self-supporting electrodes as shown in Figure 2. Assemble the supercapacitor, DC power supply, constant current pump, conductivity meter, and water storage tank as shown in Figure 4 into a deionization test system. The water inlet and outlet of the capacitor are connected to a constant flow pump and a water storage tank for solution circulation. Before the test, the water storage tank is 500ppm NaCl solution. The two electrodes of the capacitor are connected to the constant current power supply through the current collector, and the charging and discharging cycle of the capacitor is controlled in the mode shown in Figure 6, so as to realize the adsorption and desorption of ions in the salt water. Fig. 9 is the change curve of the conductivity in the NaCl solution during the charge-discharge cycle. Its average single cycle desalination capacity is 21.8mg/g.

对比例2Comparative example 2

以PAN为碳前驱体,聚苯乙烯(PS)为造孔剂,调节PAN、PS的质量比为8:2,配制总质量分数10%的DMF纺丝溶液,溶液移入注射器中,设置静电纺丝电压为12kV、纺丝距离为15cm、纺丝液喷射速度为0.5ml/min,湿度控制在30%以下,静电纺丝制备PAN/PS复合纳米纤维材料,纳米纤维置于空气气氛下进行预氧化,控制程序升温,以1℃/min升温速率升至250℃,并在250℃维持90min后自然冷却。在氮气气氛下进行碳化处理,以5℃/min升温至800℃,维持120min,冷却。由于PAN、PS二者的不相容性,在纺丝过程中形成相分离,热处理后PS分解消失即得多孔碳纳米纤维,如图1-d,但是,由于不含过渡金属盐对PAN与PMMA相分离的调节,出现了很多孔径相对较大、且分布不均的孔,此外微孔含量降低,所以其比表面积为39.83m2/g。将多孔碳纳米纤维剪成5cm×6cm大小的电极,放入500ppm的NaCl溶液中浸泡24h,即可按图2所示作为自支撑电极组装电容器。将电容器与直流电源、恒流泵、电导率仪、贮水池,按图4所示组装成电容器除盐系统。电容器的进、出水口通过接入恒流泵和贮水池进行溶液循环,测试前贮水池内为500ppm的NaCl溶液;电容器的两个电极通过集流体接入恒流电源,以图6模式控制电容器的充放电循环,实现含盐水中离子的吸、脱附。图10为充放电循环中NaCl溶液中电导率的变化曲线。由于比表面积相对较低,孔径分布相对不很均匀,因此其平均单循环脱盐量大大降低,仅仅达到2.8mg/g的水平,循环稳定性也相对较差。With PAN as the carbon precursor, polystyrene (PS) as the pore-forming agent, adjust the mass ratio of PAN and PS to 8:2, prepare a DMF spinning solution with a total mass fraction of 10%, move the solution into a syringe, and set up the electrospinning solution. The wire voltage is 12kV, the spinning distance is 15cm, the spinning liquid injection speed is 0.5ml/min, and the humidity is controlled below 30%. The PAN/PS composite nanofiber material is prepared by electrospinning, and the nanofiber is placed in an air atmosphere for pretreatment. Oxidation, controlled temperature program, raised to 250°C at a rate of 1°C/min, and maintained at 250°C for 90 minutes, then cooled naturally. Carry out carbonization treatment under nitrogen atmosphere, raise the temperature to 800°C at 5°C/min, maintain for 120min, and cool down. Due to the incompatibility between PAN and PS, phase separation is formed during the spinning process. After heat treatment, PS decomposes and disappears to form porous carbon nanofibers, as shown in Figure 1-d. However, due to the absence of transition metal salts, PAN and PS The regulation of phase separation of PMMA resulted in many pores with relatively large pore size and uneven distribution. In addition, the content of micropores decreased, so its specific surface area was 39.83m 2 /g. Cut the porous carbon nanofibers into electrodes with a size of 5cm×6cm, soak them in 500ppm NaCl solution for 24 hours, and assemble capacitors as self-supporting electrodes as shown in Figure 2. Assemble the capacitor, DC power supply, constant current pump, conductivity meter, and water storage tank as shown in Figure 4 into a capacitor desalination system. The water inlet and outlet of the capacitor are connected to a constant current pump and a water storage tank for solution circulation. Before the test, the water storage tank is 500ppm NaCl solution; the two electrodes of the capacitor are connected to the constant current power supply through the current collector, and the capacitor is controlled in the mode shown in Figure 6 The charge-discharge cycle realizes the adsorption and desorption of ions in salt water. Fig. 10 is the change curve of the conductivity in the NaCl solution during the charge-discharge cycle. Due to the relatively low specific surface area and relatively uneven pore size distribution, the average single-cycle desalination capacity is greatly reduced, only reaching the level of 2.8 mg/g, and the cycle stability is relatively poor.

Claims (10)

1.一种电容去离子用多孔碳纳米纤维的制备方法,包括:1. A method for preparing porous carbon nanofibers for capacitive deionization, comprising: (1)将碳前驱体、有机造孔剂、过渡金属盐溶解于溶剂中,得到纺丝溶液;其中,碳前驱体的质量分数为5-20%,有机造孔剂的质量分数为1-20%,过渡金属盐的质量分数为0-10%;(1) Dissolving the carbon precursor, organic pore-forming agent, and transition metal salt in a solvent to obtain a spinning solution; wherein, the mass fraction of the carbon precursor is 5-20%, and the mass fraction of the organic pore-forming agent is 1-20%. 20%, the mass fraction of transition metal salt is 0-10%; (2)将上述纺丝溶液进行静电纺丝,得到复合纳米纤维,然后依次进行预氧化、炭化、酸洗处理,即得多孔碳纳米纤维;其中,有机造孔剂为聚甲基丙烯酸甲酯PMMA、聚乳酸PLA、聚苯乙烯PS中的一种或几种。(2) Electrospinning the above spinning solution to obtain composite nanofibers, followed by pre-oxidation, carbonization, and pickling to obtain porous carbon nanofibers; wherein the organic pore-forming agent is polymethyl methacrylate One or more of PMMA, polylactic acid PLA, polystyrene PS. 2.根据权利要求1所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述步骤(1)中的碳前驱体为聚丙烯腈PAN、聚苯并咪唑PBI、丙烯腈与苯乙烯共聚物、丙烯腈与丙烯酸甲酯类的二元共聚物中的一种或几种。2. the preparation method of a kind of capacitive deionization porous carbon nanofiber according to claim 1 is characterized in that: the carbon precursor in the described step (1) is polyacrylonitrile PAN, polybenzimidazole PBI, One or more of acrylonitrile and styrene copolymers, acrylonitrile and methyl acrylate binary copolymers. 3.根据权利要求1所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述步骤(1)中的过渡金属盐为锌、铁、镍、铜、锰的卤化物、醋酸盐、磷酸盐、硫酸盐中的一种或几种。3. the preparation method of a kind of capacitive deionization porous carbon nanofiber according to claim 1 is characterized in that: the transition metal salt in the described step (1) is the halide of zinc, iron, nickel, copper, manganese One or more of substances, acetates, phosphates, and sulfates. 4.根据权利要求1所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述步骤(1)中的溶剂为N,N-二甲基甲酰胺DMF、N,N-二甲基乙酰胺DMAC中的一种或几种。4. the preparation method of a kind of capacitive deionization porous carbon nanofiber according to claim 1, is characterized in that: the solvent in the described step (1) is N, N-dimethylformamide DMF, N, One or more of N-dimethylacetamide DMAC. 5.根据权利要求1所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述步骤(2)中的静电纺丝工艺参数为:纺丝电压为10-25kV、接收距离为10-25cm、纺丝液推流速度为0.2-2ml/h,湿度控制在30-50%。5. the preparation method of a kind of capacitive deionization porous carbon nanofiber according to claim 1 is characterized in that: the electrospinning process parameter in the described step (2) is: spinning voltage is 10-25kV, The receiving distance is 10-25cm, the flow rate of spinning solution is 0.2-2ml/h, and the humidity is controlled at 30-50%. 6.根据权利要求1所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述步骤(2)中的预氧化为:在空气气氛中以0.5-2℃/min升温到240-280℃,并维持90-120min后,炉内冷却至室温;炭化为:在氮气或氩气气氛下,以2-10℃/min速率升温到700-1000℃,并维持90-120min后,氮气或氩气气氛下炉内冷却至室温;酸洗为:在酸溶液中浸泡8-24h,用纯水冲洗纳米纤维去除纤维表面的过渡金属盐。6. A method for preparing porous carbon nanofibers for capacitive deionization according to claim 1, characterized in that: the pre-oxidation in the step (2) is: in an air atmosphere at 0.5-2 °C/min Raise the temperature to 240-280°C and maintain it for 90-120 minutes, then cool the furnace to room temperature; carbonization: in nitrogen or argon atmosphere, heat up to 700-1000°C at a rate of 2-10°C/min, and maintain 90- After 120 minutes, cool in the furnace to room temperature under a nitrogen or argon atmosphere; pickling: immerse in an acid solution for 8-24 hours, rinse the nanofibers with pure water to remove transition metal salts on the surface of the fibers. 7.根据权利要求6所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述酸为盐酸、硝酸、硫酸、磷酸中的一种或几种。7 . The method for preparing porous carbon nanofibers for capacitive deionization according to claim 6 , wherein the acid is one or more of hydrochloric acid, nitric acid, sulfuric acid, and phosphoric acid. 8.根据权利要求1所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述步骤(2)得到的多孔碳纳米纤维作为自支撑电极用于组装电容器,具体为:电容器中含有1个或多个由两片大小对称的多孔碳纳米纤维组成的电极对,最外侧的电极与集流体接触并接入直流电源;同一电极对的两电极之间插入塑料网隔开作为流体通道;相邻电极对的电极之间夹入惰性导电板阻止两侧带不同电荷的离子交换;所有电极对串联接入直流电源,全部流体通道并联接入进、出水口。8. a kind of preparation method of capacitive deionization according to claim 1 uses porous carbon nanofiber, it is characterized in that: the porous carbon nanofiber that described step (2) obtains is used for assembling capacitor as self-supporting electrode, specifically : The capacitor contains one or more electrode pairs composed of two symmetrical porous carbon nanofibers, the outermost electrode is in contact with the current collector and connected to a DC power supply; a plastic mesh is inserted between the two electrodes of the same electrode pair Open as a fluid channel; an inert conductive plate is sandwiched between the electrodes of adjacent electrode pairs to prevent ion exchange with different charges on both sides; all electrode pairs are connected in series to a DC power supply, and all fluid channels are connected in parallel to the inlet and outlet. 9.根据权利要求8所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述集流体为钛网、钛片、石墨片、导电石墨纸、不锈钢片、铜片、导电碳布中的一种或几种;所述惰性导电板为钛片、石墨片、导电石墨纸、不锈钢片、铜片中的一种或几种。9. the preparation method of a kind of capacitive deionization porous carbon nanofiber according to claim 8, is characterized in that: described current collector is titanium net, titanium sheet, graphite sheet, conductive graphite paper, stainless steel sheet, copper sheet 1. One or more of conductive carbon cloth; the inert conductive plate is one or more of titanium sheet, graphite sheet, conductive graphite paper, stainless steel sheet, and copper sheet. 10.根据权利要求8所述的一种电容去离子用多孔碳纳米纤维的制备方法,其特征在于:所述电容器应用于含盐水淡化系统;其中,含盐水淡化系统包括贮水池、智能控制恒流泵、电容器、直流电源、系统控制、电导率仪、浓缩池。10. A method for preparing porous carbon nanofibers for capacitive deionization according to claim 8, characterized in that: the capacitor is applied to a salt water desalination system; wherein, the salt water desalination system includes a water storage tank, an intelligent control constant Flow pumps, capacitors, DC power supplies, system controls, conductivity meters, concentration pools.
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