CN105990031A - Diaminobenzene functionalized graphene-doped active carbon composite electrode, preparation method thereof and application of diaminobenzene-functionalized graphene-doped active carbon composite electrode to electric adsorption desalination - Google Patents
Diaminobenzene functionalized graphene-doped active carbon composite electrode, preparation method thereof and application of diaminobenzene-functionalized graphene-doped active carbon composite electrode to electric adsorption desalination Download PDFInfo
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Abstract
本发明公开了一种二氨基苯功能化石墨烯掺杂的活性炭复合电极、制备及其在电吸附脱盐上的应用。其制备方法包括以下两个步骤:(1)二氨基苯功能化石墨烯制备;(2)将活性炭与二氨基苯功能化石墨烯及粘结剂混合均匀,在模具中成型后,制备不同比表面积和吸附容量的复合电极。用此复合电极作为电吸附装置的正负极,可用于对二级生化出水脱盐等领域,其脱盐效率显著优于单纯碳电极。
The invention discloses an activated carbon composite electrode doped with diaminobenzene functionalized graphene, its preparation and its application in electro-adsorption desalination. The preparation method includes the following two steps: (1) preparation of diaminobenzene-functionalized graphene; (2) uniformly mixing activated carbon with diaminobenzene-functionalized graphene and a binder, and preparing different proportions of graphene after molding in a mold. Surface area and adsorption capacity of composite electrodes. Using the composite electrode as the positive and negative electrodes of the electro-adsorption device can be used in fields such as desalination of secondary biochemical effluent, and its desalination efficiency is significantly better than that of a simple carbon electrode.
Description
技术领域technical field
本发明涉及一种二氨基苯功能化石墨烯掺杂的活性炭复合电极、制备及其在电吸附脱盐上的应用,属于电容去离子领域。The invention relates to an activated carbon composite electrode doped with diaminobenzene functionalized graphene, its preparation and its application in electroadsorption desalination, belonging to the field of capacitive deionization.
背景技术Background technique
目前水资源短缺已经成为全球的严重问题,用海水淡化可以缓解水资源短缺的现状。对比传统的技术如反渗透法、电渗析法和旋转蒸发法,由于脱盐效率高、低能耗、无二次污染、成本低、环境友好等优点,电容去离子(Capacitive deionization,CDI,又称电吸附)法已经成为潜在的脱盐方法。脱盐的过程是运用电荷吸引,将离子吸附在电极表面。当外接电源被连接,带有相反电荷的离子会被吸引到电极表面,形成双电层。当移除电源,离子解析,重新回到溶液中,而不产生二次污染。基于双电层原理,CDI的吸附容量与电极的导电率和表面性质有密切的关系。At present, the shortage of water resources has become a serious problem in the world, and desalination of seawater can alleviate the current situation of water shortage. Compared with traditional technologies such as reverse osmosis, electrodialysis and rotary evaporation, capacitive deionization (CDI, also known as electric Adsorption) has become a potential desalination method. The process of desalination uses charge attraction to adsorb ions on the electrode surface. When an external power source is connected, oppositely charged ions are attracted to the electrode surface, forming an electric double layer. When the power is removed, the ions resolve and return to the solution without secondary pollution. Based on the principle of electric double layer, the adsorption capacity of CDI is closely related to the conductivity and surface properties of the electrode.
近些年,具有不同比表面积和孔结构的活性炭已经被广泛报道,其中包括活性炭、碳气凝胶、碳纳米管和一些复合活性炭。尽管活性炭被广泛应用,但是由于其多为微孔(<2nm)不利于离子的吸附与脱附。为了解决这个问题,科学工作者开发了具有片层结构的石墨烯作为电极材料。石墨烯具有二维结构,同时具有大的比表面积、良好的导电性、好的机械性能和化学稳定性等优点。特殊的结果和电学性能,使得石墨烯及其复合材料成为能量存储与吸附的优良材料。近些年有一些研究组开展关于石墨烯吸附脱盐的工作,如:华东理工大学的李海波(Environ.Sci.Technol.,2010,44,8692-8697),上海大学的Zhang等人(J.Mater.Chem.,2012,22,14696-14704)通过对比不同比例的石墨烯电极性能,优化材料性能,开发出具有电吸附脱盐性能的石墨烯电极。由于单纯的石墨烯具有相对低的电吸附容量,不能充分发挥其优势。更多的工作集中在复合材料的开发,但很少有报道将石墨烯功能化后作为吸附电极。In recent years, activated carbons with different specific surface areas and pore structures have been widely reported, including activated carbons, carbon aerogels, carbon nanotubes, and some composite activated carbons. Although activated carbon is widely used, it is not conducive to the adsorption and desorption of ions because it is mostly microporous (<2nm). To solve this problem, scientists have developed graphene with a sheet structure as an electrode material. Graphene has a two-dimensional structure and has the advantages of large specific surface area, good electrical conductivity, good mechanical properties and chemical stability. The special results and electrical properties make graphene and its composites excellent materials for energy storage and adsorption. In recent years, some research groups have carried out work on graphene adsorption desalination, such as: Li Haibo (Environ.Sci.Technol., 2010,44,8692-8697) of East China University of Science and Technology, Zhang et al. (J.Mater .Chem., 2012, 22, 14696-14704) By comparing the properties of graphene electrodes with different proportions, optimizing material properties, and developing graphene electrodes with electroadsorption and desalination properties. Due to the relatively low electric adsorption capacity of pure graphene, its advantages cannot be fully exerted. More work has focused on the development of composite materials, but few reports have reported the functionalization of graphene as an adsorption electrode.
发明内容Contents of the invention
本发明的目的在于提供一种具有高去除率复合电吸附电极及其制备方法,其具有高的吸附容量和脱附效率。The purpose of the present invention is to provide a composite electro-adsorption electrode with high removal rate and its preparation method, which has high adsorption capacity and desorption efficiency.
本发明的另一目的在于提供上述复合电吸附电极的应用。Another object of the present invention is to provide the application of the above-mentioned composite electrosorption electrode.
实现本发明的技术解决方案是:一种二氨基苯功能化石墨烯掺杂的活性炭复合电极,以二氨基苯功能化石墨烯作为导电添加剂,利用粘结剂将二氨基苯功能化石墨烯与活性炭均匀共混构建复合材料,经过压膜成型,将该复合材料固定在电极片上,真空烘干后即获得所述的复合电极。The technical solution for realizing the present invention is: a kind of activated carbon composite electrode doped with diaminobenzene functionalized graphene, using diaminobenzene functionalized graphene as conductive additive, utilizing binder to diaminobenzene functionalized graphene and Activated carbon is uniformly blended to construct a composite material, and the composite material is fixed on the electrode sheet through film molding, and the composite electrode is obtained after vacuum drying.
上述复合电极中,粘结剂为聚四氟乙烯、聚偏二氟乙烯和聚乙二醇等的一种或几种的混合物。In the composite electrode above, the binder is one or a mixture of polytetrafluoroethylene, polyvinylidene fluoride, polyethylene glycol, and the like.
上述复合电极中,电极片为铝、镍、钛、铜或不锈钢材质,其形态为网、箔膜和海绵体中的一种。In the above composite electrode, the electrode sheet is made of aluminum, nickel, titanium, copper or stainless steel, and its form is one of mesh, foil and sponge.
上述复合电极中,二氨基苯功能化石墨烯结构如下:In the composite electrode above, the diaminobenzene functionalized graphene structure is as follows:
上述复合电极中,以质量比计,活性炭:二氨基苯功能化石墨烯:粘结剂=(99:1:50)~(19:1:20)。In the above composite electrode, in terms of mass ratio, activated carbon:diaminobenzene functionalized graphene:binder=(99:1:50)˜(19:1:20).
二氨基苯功能化石墨烯掺杂的活性炭复合电极的制备方法,其步骤如下:The preparation method of the activated carbon composite electrode doped with diaminobenzene functionalized graphene, its steps are as follows:
(a)超声下,制备氧化石墨烯的DMF悬浮液,将该悬浮液与二氨基苯(PA)的DMF溶液混合,加热到70~100℃搅拌反应,减压过滤、洗涤、干燥后即得到二氨基苯功能化石墨烯,其中,氧化石墨和DMF溶剂的比为7.5~15mg/mL,氧化石墨烯与二氨基苯的质量比例为1:10~10:1;(a) Under ultrasound, prepare a DMF suspension of graphene oxide, mix the suspension with a DMF solution of diaminobenzene (PA), heat to 70-100°C and stir to react, filter under reduced pressure, wash and dry to obtain Diaminobenzene functionalized graphene, wherein the ratio of graphite oxide to DMF solvent is 7.5-15mg/mL, and the mass ratio of graphene oxide to diaminobenzene is 1:10-10:1;
(b)将二氨基苯功能化石墨烯研磨后,与活性炭共混,配制具有不同比例的二氨基苯功能化石墨烯与活性炭的复合物,并将其溶于有机溶剂中,混合均匀,其中,活性炭与二氨基苯功能化石墨烯的质量比为(99:1)~(19:1);(b) After the diaminobenzene functionalized graphene is ground, it is blended with activated carbon to prepare a composite of diaminobenzene functionalized graphene and activated carbon in different proportions, and it is dissolved in an organic solvent and mixed uniformly, wherein , the mass ratio of activated carbon to diaminobenzene functionalized graphene is (99:1)~(19:1);
(c)将粘结剂溶于有机溶剂中,混合均匀,其中,二氨基苯功能化石墨烯与粘结剂的质量比为(1:50)~(1:20);(c) dissolving the binder in an organic solvent and mixing evenly, wherein the mass ratio of the diaminobenzene functionalized graphene to the binder is (1:50) to (1:20);
(d)将(b)与(c)混合均匀,研磨后超声6-8小时;(d) mix (b) and (c) evenly, and ultrasonicate for 6-8 hours after grinding;
(e)将制备好的复合材料均匀涂到电极上,压制成型,并在60~80℃下真空烘干16~24h,即可得到活性炭复合电极。(e) Coating the prepared composite material evenly on the electrode, press molding, and vacuum drying at 60-80° C. for 16-24 hours to obtain the activated carbon composite electrode.
步骤(a)中,超声时间为2~10h;二氨基苯为对苯二胺、间苯二胺和邻苯二胺中的任意一种;二氨基苯与DMF溶剂的比为1:10~1:500g/mL;二氨基苯的DMF溶液的温度范围为25~80℃;搅拌反应时间为5~24h。In step (a), the ultrasonic time is 2 to 10 hours; diaminobenzene is any one of p-phenylenediamine, m-phenylenediamine and o-phenylenediamine; the ratio of diaminobenzene to DMF solvent is 1:10~ 1:500g/mL; the temperature range of the DMF solution of diaminobenzene is 25-80°C; the stirring reaction time is 5-24h.
步骤(b)中,二氨基苯功能化石墨烯与活性炭总质量与有机溶剂的质量比为In step (b), the mass ratio of diaminobenzene functionalized graphene and activated carbon total mass to organic solvent is
(1:1~2:1),有机溶剂为甲醇或乙醇。(1:1~2:1), the organic solvent is methanol or ethanol.
步骤(c)中,粘结剂与有机溶剂的质量比为(10:8~2:6),有机溶剂为甲醇或乙醇。In step (c), the mass ratio of the binder to the organic solvent is (10:8˜2:6), and the organic solvent is methanol or ethanol.
上述二氨基苯功能化石墨烯掺杂的二元活性炭复合电极在电吸附脱盐中的应用。The application of the above diaminobenzene functionalized graphene-doped binary activated carbon composite electrode in electrosorption desalination.
所去除的离子包括Na+、Mg2+、Ca2+、F-、NO3 -、NO2 -、HCO3 -、SO4 2-和PO4 3-等,吸附时间为20~150分钟,脱附时间为20~150分钟,通电电压为1.0~2.0V。The removed ions include Na + , Mg 2+ , Ca 2+ , F - , NO 3 - , NO 2 - , HCO 3 - , SO 4 2- and PO 4 3- , etc. The adsorption time is 20-150 minutes. The desorption time is 20-150 minutes, and the energizing voltage is 1.0-2.0V.
与现有技术相比,本发明的优点是:Compared with prior art, the advantage of the present invention is:
本发明利用二氨基苯功能化石墨烯的导电性强和比表面积大等特点,制备二氨基苯功能化石墨烯掺杂的活性炭复合电极。利用该方法制备的电极,具有一下特点:1.大的比表面积;2.良好的导电性能;3.高吸附容量;4.较高的吸附效率;5.较好的脱附性能。The invention utilizes the characteristics of strong conductivity and large specific surface area of the diaminobenzene functionalized graphene to prepare an activated carbon composite electrode doped with the diaminobenzene functionalized graphene. The electrode prepared by the method has the following characteristics: 1. large specific surface area; 2. good electrical conductivity; 3. high adsorption capacity; 4. high adsorption efficiency; 5. good desorption performance.
这些特点使该复合材料在城市污水及市政废水处理等领域广泛应用。These characteristics make the composite material widely used in urban sewage and municipal wastewater treatment and other fields.
附图说明Description of drawings
图1为本发明实施例1中的二氨基苯功能化石墨烯SEM图。Fig. 1 is the SEM image of diaminobenzene functionalized graphene in Example 1 of the present invention.
图2是本发明实施例1中合成的功能化石墨烯纳米材料的红外光谱图。Fig. 2 is the infrared spectrogram of the functionalized graphene nanomaterial synthesized in Example 1 of the present invention.
图3为本发明实施例2中合成的功能化石墨烯纳米材料的红外光谱图。Fig. 3 is the infrared spectrogram of the functionalized graphene nanomaterial synthesized in Example 2 of the present invention.
图4为本发明实施例6中复合电极的交流阻抗结果。Fig. 4 is the AC impedance result of the composite electrode in Example 6 of the present invention.
图5为本发明实施例7的复合电极和单纯活性炭电极对NaCl的吸附情况对比。Fig. 5 is a comparison of the adsorption of NaCl between the composite electrode of Example 7 of the present invention and the simple activated carbon electrode.
具体实施方式detailed description
实施例1-3:二氨基苯功能化石墨烯的制备:Embodiment 1-3: the preparation of diaminobenzene functionalized graphene:
实施例1Example 1
第一步,氧化石墨固体的制备;The first step, the preparation of graphite oxide solid;
在80℃,用30mL浓硫酸、10g过硫酸钾和10g五氧化二磷将20g天然石墨预氧化后,水洗至pH=7,常温干燥过夜待用;At 80°C, 20g of natural graphite was pre-oxidized with 30mL of concentrated sulfuric acid, 10g of potassium persulfate and 10g of phosphorus pentoxide, washed with water until pH = 7, and dried at room temperature overnight for use;
将460mL浓硫酸冷却到0℃左右,然后将20g预氧化的石墨加入到其中,慢慢加入60g高锰酸钾,使得体系温度不超过20℃,添加完毕后升温到35℃,搅拌2h以后,并分批慢慢加入920mL去离子水,使得体系温度不超过98℃,再搅拌15分钟以后,加入2.8L去离子水和50mL 30%双氧水。将得到的亮黄色悬浮液减压抽滤,洗涤。一直到滤液中没有硫酸根离子,且呈中性时,将产物在60℃真空中烘干,得到氧化石墨固体;Cool 460mL of concentrated sulfuric acid to about 0°C, then add 20g of pre-oxidized graphite into it, slowly add 60g of potassium permanganate so that the temperature of the system does not exceed 20°C, after the addition is completed, raise the temperature to 35°C, and stir for 2 hours, And slowly add 920mL of deionized water in batches, so that the system temperature does not exceed 98°C, and after stirring for 15 minutes, add 2.8L of deionized water and 50mL of 30% hydrogen peroxide. The resulting bright yellow suspension was filtered under reduced pressure and washed. Until there is no sulfate ion in the filtrate, and when it is neutral, the product is dried in vacuum at 60°C to obtain graphite oxide solid;
第二步,将50mg氧化石墨粉末装入圆底烧瓶,再加入15mL N,N-二甲基甲酰胺(DMF)溶剂,超声5h后,得到氧化石墨烯(GO)的悬浮液;In the second step, 50 mg of graphite oxide powder is put into a round bottom flask, and then 15 mL of N,N-dimethylformamide (DMF) solvent is added, and after ultrasonication for 5 hours, a suspension of graphene oxide (GO) is obtained;
第三步,取0.1g对苯二胺在室温下溶解于5mL DMF中,制备对苯二胺的DMF溶液;In the third step, 0.1 g of p-phenylenediamine was dissolved in 5 mL of DMF at room temperature to prepare a DMF solution of p-phenylenediamine;
第四步,将第三步中的对苯二胺溶液缓慢滴加到第二步中制备的GO悬浮液,加热到85℃,剧烈搅拌8h;In the fourth step, the p-phenylenediamine solution in the third step is slowly added dropwise to the GO suspension prepared in the second step, heated to 85°C, and vigorously stirred for 8h;
第五步,将第四步得到的粗产物经抽滤,洗涤,干燥后,即得产物。In the fifth step, the crude product obtained in the fourth step is suction-filtered, washed and dried to obtain the product.
功能化石墨烯纳米材料在溶剂中的红外光谱如图2所示,证明该纳米杂化材料已成功合成。功能化石墨烯纳米材料照片如图1的SEM所示。The infrared spectrum of the functionalized graphene nanomaterial in solvent is shown in Fig. 2, which proves that the nano-hybrid material has been successfully synthesized. The photo of the functionalized graphene nanomaterial is shown in the SEM of Figure 1.
实施例2Example 2
第一至第二步,同实施例1中步骤一至二。The first to second steps are the same as steps one to two in Example 1.
第三步,取0.1g间苯二胺在室温下溶解于5mL DMF中,制备间苯二胺的DMF溶液;In the third step, 0.1 g of m-phenylenediamine was dissolved in 5 mL of DMF at room temperature to prepare a DMF solution of m-phenylenediamine;
第四步,将第三步中的间苯二胺溶液缓慢滴加到第二步中制备的GO悬浮液,加热到85℃,剧烈搅拌8h;In the fourth step, the m-phenylenediamine solution in the third step is slowly added dropwise to the GO suspension prepared in the second step, heated to 85°C, and vigorously stirred for 8h;
第五步,同实施例1中步骤五。The fifth step is the same as step five in Example 1.
功能化石墨烯纳米材料在溶剂中的红外光谱如图3所示,证明该纳米杂化材料已成功合成。The infrared spectrum of the functionalized graphene nanomaterial in solvent is shown in Fig. 3, which proves that the nano-hybrid material has been successfully synthesized.
实施例3Example 3
第一至第二步,同实施例1中步骤一至二。The first to second steps are the same as steps one to two in Example 1.
第三步,取0.1g邻苯二胺在室温下溶解于5mL DMF中,制备邻苯二胺的DMF溶液;In the third step, 0.1 g of o-phenylenediamine was dissolved in 5 mL of DMF at room temperature to prepare a DMF solution of o-phenylenediamine;
第四步,将第三步中的邻苯二胺溶液缓慢滴加到第二步中制备的GO悬浮液,加热到100℃,剧烈搅拌24h;In the fourth step, the o-phenylenediamine solution in the third step is slowly added dropwise to the GO suspension prepared in the second step, heated to 100°C, and vigorously stirred for 24 hours;
第五步,同实施例1中步骤五。The fifth step is the same as step five in Example 1.
实施例4-12:复合电极的制备及其应用Example 4-12: Preparation and Application of Composite Electrode
实施例4Example 4
复合电极的制备:(1)分别称取实施例1中的二氨基苯功能化石墨烯和活性碳粉末的质量为1g和19g,按照1:19的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL甲醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:2(PTFE的质量为66g)溶于200mL甲醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。Preparation of composite electrode: (1) take the quality of diaminobenzene functionalized graphene and activated carbon powder in Example 1 respectively to be 1g and 19g, and mix them uniformly according to the ratio of 1:19; (2) mix the two The material was mixed and ground in a mortar for 30 minutes; (3) the homogeneously mixed material was dissolved in 300mL of methanol, and continued to stir until uniformly mixed; (4) ultrasonic for 5 hours; (5) weigh the binder PTFE according to the ratio 1: 2 (the mass of PTFE is 66g) is dissolved in 200mL methanol, put it into the beaker and disperse for 1 hour; (6) Stir with a glass rod to mix the two evenly, and continue ultrasonication for 3 hours; (6) Mix evenly Spread the material evenly on the electrode sheet, and use a machine to form a film; (7) Air-dry the electrode for 24 hours; (8) Dry it in vacuum at 80°C for 24 hours, and set it aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.6V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到80%。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in the self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the electrification voltage of the two poles is 1.6V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) The adsorption time is 40 minutes; (5) The electrode is short-circuited for desorption, and the time is 60 minutes; (6) The desalination rate under the above conditions can reach 80%.
实施例5Example 5
复合电极的制备:(1)分别称取实施例2中的二氨基苯功能化石墨烯和活性碳粉末的质量为0.2g和19.8g,按照1:99的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL甲醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:1(PTFE的质量为33g)溶于200mL甲醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。The preparation of composite electrode: (1) take the mass of diaminobenzene functionalized graphene and activated carbon powder in Example 2 to be 0.2g and 19.8g respectively, mix according to the ratio of 1:99; (2) Mix the two substances in a mortar and grind for 30 minutes; (3) Dissolve the uniformly mixed material in 300mL methanol, continue to stir, and mix evenly; (4) Ultrasound for 5 hours; (5) Weigh the binder PTFE according to the proportion Dissolve 1:1 (the mass of PTFE is 33g) in 200mL methanol, put it into a beaker and disperse for 1 hour; (6) Stir with a glass rod to mix the two evenly, and continue to ultrasonic for 3 hours; (6) Mix evenly The finished material is spread evenly on the electrode sheet, and is pressed into a film by a machine; (7) The electrode is air-dried for 24 hours; (8) Dry it in a vacuum at 80°C for 24 hours, and set aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.6V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到85%。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in the self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the electrification voltage of the two poles is 1.6V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) The adsorption time is 40 minutes; (5) The desorption time is 60 minutes when the electrode is short-circuited; (6) The desalination rate can reach 85% under the above conditions.
实施例6Example 6
复合电极的制备:(1)分别称取实施例2中的二氨基苯功能化石墨烯和活性碳粉末的质量为2g和18g,按照1:9的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL乙醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:1(PTFE的质量为33g)溶于200mL乙醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。The preparation of composite electrode: (1) take the mass of diaminobenzene functionalized graphene and activated carbon powder in Example 2 to be 2g and 18g respectively, mix according to the ratio of 1:9; (2) mix the two kinds The material was mixed and ground in a mortar for 30 minutes; (3) the homogeneously mixed material was dissolved in 300mL ethanol, continued to stir, and mixed uniformly; (4) ultrasonicated for 5 hours; (5) the binder PTFE was weighed according to the ratio 1: 1 (the mass of PTFE is 33g) dissolved in 200mL ethanol, put it into a beaker and disperse for 1 hour; (6) Stir with a glass rod to mix the two evenly, and continue ultrasonication for 3 hours; (6) Mix evenly Spread the material evenly on the electrode sheet, and use a machine to form a film; (7) Air-dry the electrode for 24 hours; (8) Dry it in vacuum at 80°C for 24 hours, and set it aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.8V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到88%。图4为电极的交流阻抗结果。从结果中可以看到该电极电阻较小适合用作电吸附脱盐电极。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in a self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the voltage of the two poles is 1.8V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) adsorption time is 40 minutes; (5) electrode short circuit desorption time is 60 minutes; (6) desalination rate can reach 88% under the above conditions. Figure 4 shows the AC impedance results of the electrodes. It can be seen from the results that the electrode has a small resistance and is suitable for use as an electrode for electroadsorption desalination.
实施例7Example 7
复合电极的制备:(1)分别称取实施例2中的二氨基苯功能化石墨烯和活性碳粉末的质量为1g和19g,按照1:19的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL乙醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:1(PTFE的质量为33g)溶于200mL乙醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。Preparation of composite electrode: (1) take the quality of diaminobenzene functionalized graphene and activated carbon powder in Example 2 to be 1g and 19g respectively, and mix them uniformly according to the ratio of 1:19; (2) mix the two The material was mixed and ground in a mortar for 30 minutes; (3) the homogeneously mixed material was dissolved in 300mL ethanol, continued to stir, and mixed uniformly; (4) ultrasonicated for 5 hours; (5) the binder PTFE was weighed according to the ratio 1: 1 (the mass of PTFE is 33g) dissolved in 200mL ethanol, put it into a beaker and disperse for 1 hour; (6) Stir with a glass rod to mix the two evenly, and continue ultrasonication for 3 hours; (6) Mix evenly Spread the material evenly on the electrode sheet, and use a machine to form a film; (7) Air-dry the electrode for 24 hours; (8) Dry it in vacuum at 80°C for 24 hours, and set it aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.8V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到90%。图5为复合电极(AC/GEA2)与单纯活性炭电极(AC)对NaCl的吸附情况对比。结果表明该复合电极的脱盐效果明显优于单纯活性炭电极。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in a self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the voltage of the two poles is 1.8V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) The adsorption time is 40 minutes; (5) The electrode is short-circuited for desorption, and the time is 60 minutes; (6) The desalination rate under the above conditions can reach 90%. Figure 5 is a comparison of the adsorption of NaCl by the composite electrode (AC/GEA2) and the simple activated carbon electrode (AC). The results show that the desalination effect of the composite electrode is significantly better than that of the pure activated carbon electrode.
实施例8Example 8
复合电极的制备:(1)分别称取实施例2中的二氨基苯功能化石墨烯和活性碳粉末的质量为0.2g和19.8g,按照1:99的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL甲醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:2(PTFE的质量为66g)溶于200mL甲醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。The preparation of composite electrode: (1) take the mass of diaminobenzene functionalized graphene and activated carbon powder in Example 2 to be 0.2g and 19.8g respectively, mix according to the ratio of 1:99; (2) Mix the two substances in a mortar and grind for 30 minutes; (3) Dissolve the uniformly mixed material in 300mL methanol, continue to stir, and mix evenly; (4) Ultrasound for 5 hours; (5) Weigh the binder PTFE according to the proportion 1:2 (the mass of PTFE is 66g) was dissolved in 200mL methanol, put it in a beaker and dispersed for 1 hour; (6) Stir with a glass rod to mix the two evenly, and continue to ultrasonic for 3 hours; (6) Mix evenly The finished material is spread evenly on the electrode sheet, and is pressed into a film by a machine; (7) The electrode is air-dried for 24 hours; (8) Dry it in a vacuum at 80°C for 24 hours, and set aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.8V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到87%。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in a self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the voltage of the two poles is 1.8V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) adsorption time is 40 minutes; (5) electrode short circuit desorption time is 60 minutes; (6) desalination rate can reach 87% under the above conditions.
实施例9Example 9
复合电极的制备:(1)分别称取实施例3中的二氨基苯功能化石墨烯和活性碳粉末的质量为1g和19g,按照1:19的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL甲醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:2(PTFE的质量为66g)溶于200mL甲醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。Preparation of composite electrode: (1) take the quality of diaminobenzene functionalized graphene and activated carbon powder in Example 3 to be 1g and 19g respectively, and mix them uniformly according to the ratio of 1:19; (2) mix the two The material was mixed and ground in a mortar for 30 minutes; (3) the homogeneously mixed material was dissolved in 300mL of methanol, and continued to stir until uniformly mixed; (4) ultrasonic for 5 hours; (5) weigh the binder PTFE according to the ratio 1: 2 (the mass of PTFE is 66g) is dissolved in 200mL methanol, put it into the beaker and disperse for 1 hour; (6) Stir with a glass rod to mix the two evenly, and continue ultrasonication for 3 hours; (6) Mix evenly Spread the material evenly on the electrode sheet, and use a machine to form a film; (7) Air-dry the electrode for 24 hours; (8) Dry it in vacuum at 80°C for 24 hours, and set it aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.6V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到80%。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in the self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the electrification voltage of the two poles is 1.6V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) The adsorption time is 40 minutes; (5) The electrode is short-circuited for desorption, and the time is 60 minutes; (6) The desalination rate under the above conditions can reach 80%.
实施例10Example 10
复合电极的制备:(1)分别称取实施例1中的二氨基苯功能化石墨烯和活性碳粉末的质量为1g和19g,按照1:19的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL甲醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:1(PTFE的质量为33g)溶于200mL甲醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。Preparation of composite electrode: (1) take the quality of diaminobenzene functionalized graphene and activated carbon powder in Example 1 respectively to be 1g and 19g, and mix them uniformly according to the ratio of 1:19; (2) mix the two The material was mixed and ground in a mortar for 30 minutes; (3) the homogeneously mixed material was dissolved in 300mL of methanol, and continued to stir until uniformly mixed; (4) ultrasonic for 5 hours; (5) weigh the binder PTFE according to the ratio 1: 1 (the mass of PTFE is 33g) dissolved in 200mL of methanol, put it into a beaker and disperse for 1 hour; (6) Stir with a glass rod to mix the two evenly, then continue ultrasonication for 3 hours; (6) Mix evenly Spread the material evenly on the electrode sheet, and use a machine to form a film; (7) Air-dry the electrode for 24 hours; (8) Dry it in vacuum at 80°C for 24 hours, and set it aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.8V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到85%。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in a self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the voltage of the two poles is 1.8V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) The adsorption time is 40 minutes; (5) The desorption time is 60 minutes when the electrode is short-circuited; (6) The desalination rate can reach 85% under the above conditions.
实施例11Example 11
电极的制备:(1)分别称取实施例1中的二氨基苯功能化石墨烯和活性碳粉末的质量为0.4g和19.6g,按照1:99的比例混合均匀;(2)将两种物质混合放在研钵中研磨30分钟;(3)混合均匀的材料溶于300mL甲醇中,继续搅拌,混合均匀;(4)超声5小时;(5)称取粘结剂PTFE按照比例1:2(PTFE的质量为66g)溶于200mL甲醇中,将其放入烧杯中分散1小时;(6)用玻璃棒搅拌使两者混合均匀后,继续超声3小时;(6)混合均匀后的材料在电极片上涂抹均匀,用机器压膜成型;(7)电极风干24小时;(8)在真空80℃烘干24小时,备用。The preparation of electrode: (1) take the mass of diaminobenzene functionalized graphene and activated carbon powder in embodiment 1 respectively to be 0.4g and 19.6g, mix according to the ratio of 1:99; (2) mix two The materials were mixed and ground in a mortar for 30 minutes; (3) the homogeneously mixed material was dissolved in 300mL methanol, and continued to stir until uniformly mixed; (4) ultrasonicated for 5 hours; (5) the binder PTFE was weighed according to the ratio of 1 : 2 (the quality of PTFE is 66g) is dissolved in 200mL methanol, it is put into the beaker and disperses for 1 hour; (6) After stirring with a glass rod to make the two mix evenly, continue ultrasonication for 3 hours; (6) After mixing evenly Spread the material evenly on the electrode sheet, and press it into a film with a machine; (7) air-dry the electrode for 24 hours; (8) dry it in vacuum at 80°C for 24 hours, and set it aside.
对复合电极做电吸附研究:将新制备的复合电极从烘箱中取出,冷却,并在超纯水中浸泡24小时。然后组装电吸附装置,进行脱盐实验。具体步骤如下:(1)制备的复合材料电极片安装到自制电吸附装置中,作为正负极;(2)接上直流电源,两极通电电压为1.6V;(3)配置240mg/L NaCl溶液,取1000mL溶液做脱盐实验;(4)吸附时间为40分钟;(5)电极短接脱附,时间为60分钟;(6)以上条件脱盐率可以达到80%。Electrosorption studies on composite electrodes: The freshly prepared composite electrodes were taken out of the oven, cooled, and soaked in ultrapure water for 24 hours. Then assemble the electrosorption device and conduct the desalination experiment. The specific steps are as follows: (1) The prepared composite electrode sheet is installed in the self-made electrosorption device as the positive and negative electrodes; (2) Connected to a DC power supply, and the electrification voltage of the two poles is 1.6V; (3) Prepare 240mg/L NaCl solution , take 1000mL solution for desalination experiment; (4) The adsorption time is 40 minutes; (5) The electrode is short-circuited for desorption, and the time is 60 minutes; (6) The desalination rate under the above conditions can reach 80%.
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109817471A (en) * | 2018-12-26 | 2019-05-28 | 中国电子科技集团公司第十八研究所 | Modification method of graphene-based lithium ion capacitor positive electrode material |
TWI821367B (en) * | 2019-08-16 | 2023-11-11 | 王鴻博 | Method for recycling of few rare precious metals and water from inorganic wastewater |
CN117383660A (en) * | 2023-11-09 | 2024-01-12 | 南京理工大学 | A graphene-based composite electrode and its preparation method and application |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101527202A (en) * | 2009-04-24 | 2009-09-09 | 南京理工大学 | Oxidized grapheme/polyaniline super capacitor composite electrode material and preparation method and application thereof |
CN102279215A (en) * | 2010-06-10 | 2011-12-14 | 国家纳米科学中心 | Amido-functionalized graphene oxide composite material and preparation method and application thereof |
US20130153426A1 (en) * | 2011-12-18 | 2013-06-20 | Zhuo Sun | Membrane enhanced deionization capacitor device |
CN103578788A (en) * | 2013-11-15 | 2014-02-12 | 东华大学 | Porous carbon combined electrode containing charge conductive nano-particles, preparation of porous carbon combined electrode and application of porous carbon combined electrode |
-
2015
- 2015-03-31 CN CN201510148945.2A patent/CN105990031A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101527202A (en) * | 2009-04-24 | 2009-09-09 | 南京理工大学 | Oxidized grapheme/polyaniline super capacitor composite electrode material and preparation method and application thereof |
CN102279215A (en) * | 2010-06-10 | 2011-12-14 | 国家纳米科学中心 | Amido-functionalized graphene oxide composite material and preparation method and application thereof |
US20130153426A1 (en) * | 2011-12-18 | 2013-06-20 | Zhuo Sun | Membrane enhanced deionization capacitor device |
CN103578788A (en) * | 2013-11-15 | 2014-02-12 | 东华大学 | Porous carbon combined electrode containing charge conductive nano-particles, preparation of porous carbon combined electrode and application of porous carbon combined electrode |
Non-Patent Citations (2)
Title |
---|
MA HUI-LING. ET AL.: ""Functionalization and Reduction of Graphene Oxide with p-Phenylene Diamine for Electrically Conductive and Thermally Stable Polystyrene Composites"", 《ACS APPLIED MATERIALS & INTERFACES》 * |
第2263-2271页: ""功能化石墨烯/活性炭复合电极及不对称电容器脱盐"", 《物理化学学报》 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109817471A (en) * | 2018-12-26 | 2019-05-28 | 中国电子科技集团公司第十八研究所 | Modification method of graphene-based lithium ion capacitor positive electrode material |
TWI821367B (en) * | 2019-08-16 | 2023-11-11 | 王鴻博 | Method for recycling of few rare precious metals and water from inorganic wastewater |
CN117383660A (en) * | 2023-11-09 | 2024-01-12 | 南京理工大学 | A graphene-based composite electrode and its preparation method and application |
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