CN111018059A - Preparation method of carbon fiber inorganic polymer composite electrode - Google Patents

Preparation method of carbon fiber inorganic polymer composite electrode Download PDF

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CN111018059A
CN111018059A CN201911171291.XA CN201911171291A CN111018059A CN 111018059 A CN111018059 A CN 111018059A CN 201911171291 A CN201911171291 A CN 201911171291A CN 111018059 A CN111018059 A CN 111018059A
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carbon fiber
polymer composite
inorganic polymer
rhodamine
composite electrode
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张耀君
孟倩
陈浩
贺攀阳
雷嘉芊
李婵娟
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Xian University of Architecture and Technology
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Abstract

The invention discloses a preparation method of a carbon fiber inorganic polymer composite electrode, which comprises the following steps of mixing carbon fiber, metakaolin, silica fume, solid sodium hydroxide and deionized water according to a mass ratio of 0.2-0.6: 6: 4: 2: 8, stirring, mixing, uniformly dip-coating on the surface of the pretreated stainless steel substrate, drying, curing and reacting to obtain the carbon fiber inorganic polymer composite electrode, wherein the preparation process has no three-waste discharge and is environment-friendly, and the method is a new way for utilizing the solid waste silica fume with high added value. The rhodamine B organic dye is applied to an anode for photoelectrocatalytic organic dye wastewater degradation, and the photoelectrocatalytic degradation rate of the rhodamine B organic dye can reach 99.77%.

Description

Preparation method of carbon fiber inorganic polymer composite electrode
Technical Field
The invention belongs to the field of preparation of a photoelectrocatalysis electrode material and resource utilization of solid waste, relates to preparation of an electrocatalysis anode material, and particularly relates to a preparation method of a carbon fiber inorganic polymer composite electrode and application of the carbon fiber inorganic polymer composite electrode in dye degradation.
Background
The photoelectrocatalysis oxidation technology is one of effective ways for degrading organic pollutants in water. The core of the photoelectrocatalysis oxidation technology is the preparation of the photoanode material. The material with photocatalytic activity is loaded on the surface of a conductive carrier by methods such as an anodic oxidation method, a thermal decomposition method, a pulse electrodeposition method, a hydrothermal deposition method, a hydrothermal method, a high-temperature liquid phase growth method, a coating method, a dipping and pulling method and the like to prepare the photoanode. At present, the materials loaded by the photoanode mainly comprise two main types of metal compounds and non-metal compounds. The metal oxides include mainly titanium oxides, zinc oxides, iron oxides, bismuth compounds, and other metal compounds. The non-metallic compounds include carbon nitrides and silicon carbides.
TiO2The most studied materials are used in the field of photoelectrocatalysis. A large number of scholars can carry out TiO modification by means of compound semiconductors, precious metal deposition, dye photosensitization, nonmetal doping and the like2The modification is carried out to widen the photoresponse range of the photo-catalytic photo-anode and improve the separation efficiency of photo-generated electrons and holes, thereby preparing the photo-catalytic photo-anode with good performance[1-5]. There are also patents relating to TiO2Preparation of photoanode material[6-11]
ZnO and TiO2The direct band gap of (A) can be approached, and the method can be used in the field of photoelectrocatalysis. Yan Weiping[12]In for iso-use2O3The sensitized ZnO nanorod array is used for preparing the photoelectrocatalysis anode material with good catalytic performance. Li Wei soldier[13]Equal, Korean[14]The catalytic performance of the zinc oxide photo-anode is improved by adopting a semiconductor compounding method. Wudi[15]A method for preparing a visible light response type zinc oxide semiconductor photoelectric material is reported. Panlun[16]A Z-type junction ZnO-WO is disclosed3A method for preparing an electrode.
In addition, some researchers studied Fe2O3The photoelectrocatalysis performance of the photoanode. For example, a gold ring[17]And the like adopts Al and Ta co-doped to prepare visible light response type Ta/Al-Fe2O3Photocatalytic films are used for photoelectrocatalysis. Lican (Lican)[18]Et al report an α -Fe2O3The photo-anode and the preparation method thereof.
The bismuth compound used for the photoelectrocatalysis photoanode is mainly bismuth vanadate, and in addition, bismuth tungstate and bismuth phosphate. The preparation method of bismuth compound photo-anode is reported in the literature and patent[19-26]
Other metal oxides being predominantly SnO2And CuWO4. Xudesong[27]The mulsane light[28]Equal, yellow clever[29]Et al report modified SnO2Preparation of photo-anode, Liu Zhi Hua[30]Etc. disclose Co-doped nanorod-shaped CuWO4A method for preparing a photo-anode film.
Carbon nitride is a non-metal oxide photo-anode material which is researched more. Cattle courage[31]The platinum atom modified carbon nitride nanorod photoelectrocatalysis electrode is prepared by adopting a noble metal modification means. In addition, SiC is also used by scholars for the preparation of photoanodes, such as: good and bright in appearance[32]And the like to prepare the N-doped SiC monocrystal nano-pore array photoelectrocatalysis anode.
In conclusion, the applicant consults a large amount of domestic and foreign literature data through a system, and does not find any relevant report about the preparation method of any carbon fiber inorganic polymer composite electrode and the application of the carbon fiber inorganic polymer composite electrode in organic dye degradation.
The following are the main references relevant to the present invention:
[1]zhao Yi Ming, Yang Relay Kai, horseFuhui, Chen Zhang Miaoxiong, Weizi Juan, Zhang Yufei, Cheng Ming, Yangxue, Xiaonan, Wang Guo Fang, Wang Xin, Huang Keke, porous silicon/TiO2Preparation of nano-wire photo-anode and its photoelectrocatalysis performance, inorganic chemistry report, 2019, 35 (04): 613-620.
[2]Chuhuanan, Li Deng, Liu Guantao, Liqun, Shijiaying and TiN(0.3)/CeO2Construction of photo-anode material and its photo-electro-catalytic properties, catalytic statement 2015, 36 (04): 550-554.
[3]Sunjijie, Hequan, Li Jian, Liuchun Guang, Shenyang, ZnFe2O4/TiO2Preparation of nanotube array electrode and research on photoelectrocatalytic degradation of phenol, chemical bulletin, 2013, 71 (02): 78-85.
[4]Gold billow, xu 38932, cun peng, chan min, feo (oh) -TiO2Preparation of a/CoPi composite light anode and the photoelectrocatalytic oxidation water performance thereof, the report of physical chemistry 2012, 28(10): 2276-2284.
[5]Zhang Mao Jun, Chen Ming, Wu Yuan Chun, Ag-CNT/TiO2The photoelectrocatalytic degradation of the composite electrode to methylene blue, a novel carbon material 2010, 25(05): 348-.
[6] A method for preparing a photoelectrocatalysis material electrode, a method for preparing a material electrode of royal phoenix martial arts, maoyu road, xumei, wangzhi, zhuigao, and wujun, a Chinese patent publication: CN108048867B, 2019.
[7] Zhang Xiaofan, Kongweiqian, Wanlin, Guo Zheng, Zhang Zanren, Yangbaocheng, phosphorized copper modified titanium dioxide photoelectrode, preparation method and application in photoelectrocatalysis decomposition water, Chinese patent publication No: CN108193219B, 2019.
[8]Zhao Xu, Rojing, a TiO with photoelectrocatalysis properties2Ru-IrO2The preparation method and the application of the electrode are disclosed in Chinese patent publication No.: CN108408845A, 2018-08-17.
[9]Zhang Xiaofan, Zhang guan Yan, Kouyanqian, Yan Bao Cheng, adopts Ni1-xFexA method for preparing hydrogen by photoelectrocatalysis decomposition of water by OOH modified titanium dioxide photoanode, Chinese patent publication No: CN107881524A, 2018.
[10]Tianyuan, Tianyue, Xiaozhujun, Lihouxing, Wanyan, Huangshuangshuang, slaughtered pottery, Qianxuefeng, Cu2ZnSnS4Sensitized TiO2A photoanode, an in-situ preparation method and application thereof, wherein the photoanode comprises the following components in parts by weight: CN105261483B, 2018.
[11]Bin, Zhou Zi, Zai Sheng, Ye Zhen, a few-layer GeTe nanosheet @ TiO2A nano-rod composite photo-anode and a preparation method thereof, wherein the preparation method comprises the following steps: CN109999846A, 2019.
[12]Yan Weiping, Wangdexjun, Chenping, Luyongchun, Xiezeng, Linyanhong, In2O3The performance and the photoelectrocatalysis activity of the sensitized ZnO nano-rod array are reported by the physical chemistry, 2013, 29(05): 1021-1027.
[13]Li Wei soldier, Yu, strong In construction, ZnO/In2O3Preparation of the composite hollow sphere and the photoelectrocatalytic glucose degradation performance thereof, physical and chemical reports 2012, 28(11): 2676-2682.
[14]Korean Shixining, Li you Jiu, Linxiao, Wangzi Yu, Li Ziqin, Wanhao, conductive glass loaded Fe2O3Preparation and photoelectrocatalysis performance of the/ZnO composite photoelectrode, and the report of high school chemistry 2018, 39(04): 771-778.
[15] Wudi, great forest, a preparation method of a visible light response type zinc oxide semiconductor photoelectric material, Chinese patent publication No.: CN105810559A, 2016.
[16]Panlun, Chenying, Zhongjijun, Zhang Xiang, Wang exterior, a Z-junction ZnO-WO3An electrode, a preparation method thereof and application thereof in photoelectrocatalysis, wherein the electrode is prepared from the following components in parts by weight: CN106881078B, 2019.
[17]Jinhuan, king beautiful silk, Jiyun, Chenmei, anecdotal, Wangqin, conyanqing, Ta/Al-Fe2O3Preparation of film electrode and its performance of photoelectrocatalytic degradation of methylene blue, physical chemistry report 2015, 31(05): 955-964.
[18]Lican, Korean Crystal Peak, Wangzhiling, a α -Fe2O3The photo-anode and the preparation method thereof, Chinese patent publication No: CN104617355B, 2017.
[19]Huang Y,Yu Y F,Xin Y,Meng N N,Yu Y,Zhang B,Promoting chargecarrier utilization by integrating layered double hydroxide nanosheet arrayswith porous BiVO4photoanode for efficient photoelectrochemical watersplitting,Science China Materials,2017,60(3),193-207。
[20]Liu S,Zhao M Y,He Z T,Zhong Y,Ding H,Chen D M.Preparation of a p-n heterojunction 2D BiOI nanosheet/1DBiPO4nanorod composite electrode forenhanced visible light photoelectrocatalysis,Chinese Journal of Catalysis,2019,40(3),446-457。
[21] Liu Chang Hai, Luo Heng, Chen Zhi Chian, a MIL series MOF composite molybdenum-doped bismuth vanadate photo-anode preparation method, Chinese patent publication No.: CN110047657A, 2019.
[22] Zhang Liang, Wang Qi Bian, Huang Jing Wei, Shebield, Wang Lei, a preparation method of a CoPi/Ag/bismuth vanadate composite photoelectric anode material, Chinese patent publication No: CN109865525A, 2019.
[23] Wangqizhao, Zhoushenqian, Shebidede, Wanyili, Huangjing Wei, a preparation method of ZIF-67/bismuth vanadate composite material and application of the composite material as a photoelectric anode material, wherein the Chinese patent publication numbers are as follows: CN109280937A, 2019.
[24]Houhulin, Masuang and Yang you, a ZnO modified WO3/BiVO4A preparation method of a heterojunction and application thereof in photoelectrocatalysis are disclosed in Chinese patent publication No.: CN109778223A, 2019.
[25]Wangpeng, Liangxizhuang, Huangbaibiao, Zhang Xiaoyang, Qinxiangyan, Wangzhike, Zhengzhaoke, Yunity of Liuyu, Zhang Qian, a large-size nanometer porous BiVO4A photoanode, a preparation method and application thereof, wherein the preparation method comprises the following steps: CN109440130A, 2019.
[26] Schweidong, xiateng, xudongfeng, chenbiyi, xieli, a preparation method of a phosphorus-doped bismuth vanadate photo-anode, and Chinese patent publications: CN108004526A, 2018.
[27] Xudeson, load type visible light response photoelectrocatalysis material and preparation method thereof, Chinese patent publication No: CN106000411B, 2019.
[28] The mullerite, Lihepu, Yangmu, Huangcong, a graphite-phase carbon nitride modified antimony-doped stannic oxide composite photoelectrocatalysis electrode, its preparation method and application, the Chinese patent publication No: CN109824120A, 2019.
[29] Clever, plum sea prail, poplar meglumine, mousse light, Yao crystal, a bismuth tungstate modified antimony-doped stannic oxide composite photoelectrocatalysis electrode, preparation method and application, Chinese patent publication No: CN109772295A, 2019.
[30]Cortex et radix Polygalae, plantula Papaveris, cortex et radix Polygalae, and Co-doped nanorod-shaped CuWO4The preparation method of the photo-anode film is disclosed in Chinese patent publication No.: CN109295474A, 2019.
[31] Bulleya, a preparation method of a platinum atom modified carbon nitride nanorod photoelectrocatalysis electrode, and the Chinese patent publication No: CN110143648A, 2019.
[32] The patent publication of China is that the N-doped SiC monocrystal nano-pore array and the prepared photoelectrocatalysis anode have the advantages of being good and bright, rich in Zhao and Liang, and good in Lin, and Yang is good, and the patent publication number of China: CN109811356A, 2019.
Disclosure of Invention
The invention aims to provide a preparation method of a carbon fiber inorganic polymer composite electrode, so as to reveal the change rule of the doping amount of carbon fibers in an electrocatalytic anode material and the degradation rate of photoelectrocatalytic organic dye wastewater.
In order to realize the task, the invention adopts the following technical solution:
the preparation method of the carbon fiber inorganic polymer composite electrode is characterized by comprising the following steps of: 6: 4: 2: and 8, stirring and mixing, uniformly dip-coating on the surface of the pretreated stainless steel substrate, drying, and curing to obtain the carbon fiber inorganic polymer composite electrode.
The method specifically comprises the following steps:
(1) weighing carbon fiber, metakaolin and silica fume according to the formula, mixing, putting into a vibration mill, and milling for 20 seconds to form a solid mixture;
(2) weighing solid sodium hydroxide according to the formula amount, putting the solid sodium hydroxide into a beaker, adding ionized water according to the formula amount into the beaker, and completely dissolving the solid sodium hydroxide under stirring to obtain a sodium hydroxide solution;
(3) pouring the solid mixture into a sodium hydroxide solution, and fully stirring to form uniform slurry;
(4) and (3) dip-coating the slurry on the surface of the pretreated steel sheet substrate, placing the pretreated steel sheet substrate in a drying oven under a sealed condition, and curing and reacting for 8 hours at 80 ℃ to obtain the carbon fiber inorganic polymer composite electrode.
The research of the applicant finds that the obtained carbon fiber inorganic polymer composite electrode can be applied to the application of degrading rhodamine B organic dye wastewater through photoelectrocatalysis.
The specific application comprises the following steps:
(1) connecting the prepared carbon fiber inorganic polymer composite electrode with the positive electrode of a direct current stabilized power supply to serve as the anode of a photoelectrocatalysis device, and connecting the pretreated steel sheet electrode with the negative electrode of the direct current stabilized power supply to serve as the cathode of the photoelectrocatalysis device;
(2) the initial concentration C is prepared by a volumetric flask0Adding a certain amount of sodium persulfate into the rhodamine B dye aqueous solution; using UV-visible spectrophotometer at lambdamaxInitial absorbance a was measured at 554nm0
(3) Placing the anode and the cathode in parallel in a container with a certain volume and concentration of CoIn the rhodamine B dye aqueous solution, a certain bias voltage is applied to an electrode, a xenon lamp is used for simulating sunlight to irradiate for a certain time at room temperature, the reaction solution is taken out and put into a cuvette, and an ultraviolet-visible spectrophotometer is used for measuring the color temperature of the rhodamine B dye aqueous solution at lambdamaxAbsorbance A at time t was measured at 554nmtDye concentration of Ct
(4) After the absorbance is measured, all the reaction liquid is put into the reactor again;
(5) and (5) repeating the step (3) and the step (4) until the absorbance of the rhodamine B dye aqueous solution does not change along with the change of time any more, and calculating the degradation rate of the rhodamine B dye by adopting the following formula:
Figure BDA0002288781640000071
the preparation method of the carbon fiber inorganic polymer composite electrode has the innovation points that: a carbon fiber inorganic polymer composite electrode which is not reported in the literature is prepared and can be used as a photoelectrocatalysis anode. The conductivity of the carbon fiber inorganic polymer composite electrode is adjusted by controlling the doping amount of the carbon fiber, so that the controllability of photoelectrocatalysis is achieved. Meanwhile, the preparation process has no three-waste discharge, is environment-friendly, and realizes high value-added recycling of solid waste silicon ash.
Drawings
FIG. 1 is a process flow chart of the preparation of the carbon fiber inorganic polymer composite electrode and the photoelectrocatalytic degradation of organic dye wastewater;
FIG. 2 is a photograph of a carbon fiber inorganic polymer composite electrode;
FIG. 3 is an XRD diffraction pattern of the feedstock (silica fume and metakaolin mixture) and CFICE samples;
FIG. 4 is the photoelectrocatalytic degradation rate of CFICE sample on rhodamine B dye;
the present invention will be described in further detail with reference to the following drawings and examples.
Detailed Description
It should be noted that the following examples are only for better illustrating the present invention, and the present invention is not limited to these examples.
The embodiment provides a preparation method of a carbon fiber inorganic polymer composite electrode, which is characterized in that carbon fibers, metakaolin, silica fume, solid sodium hydroxide and deionized water are selected as main raw materials, wherein the mass ratio of the carbon fibers, the metakaolin, the silica fume, the solid sodium hydroxide and the deionized water is 0.2-0.6: 6: 4: 2: 8.
and stirring and mixing the carbon fiber, the metakaolin, the silica fume, the solid sodium hydroxide and the deionized water, uniformly dip-coating the mixture on the surface of the pretreated stainless steel substrate, and drying and curing the mixture to obtain the carbon fiber inorganic polymer composite electrode.
The raw material sources are as follows:
(1) carbon fibers, available from tianjin forest new materials science and technology ltd;
(2) metakaolin, purchased from Chenyi refractory abrasives, Inc.;
(3) silica fume, available from minnew energy materials, ltd, available in huohao city, inner mongolia;
(4) solid sodium hydroxide, purchased from chemical reagents of national drug group, ltd, analytically pure reagent;
(5) the stainless steel substrate is a 304 type stainless steel sheet with the thickness of 15mm (length) multiplied by 15mm (width) multiplied by 0.2mm (thickness);
the pretreatment process of the 304 type stainless steel sheet comprises the steps of polishing the surface of the steel sheet by using sand paper, then placing the steel sheet in a sodium hydroxide solution with the mass fraction of 40%, carrying out water bath reaction for 1h at 80 ℃ under magnetic stirring, washing with deionized water after taking out, then placing the steel sheet in an oxalic acid solution with the mass fraction of 10%, carrying out water bath reaction for 30min at 95 ℃ under magnetic stirring, washing with deionized water after taking out, drying, and placing in absolute ethyl alcohol for storage and later use.
The preparation method comprises the following steps:
(1) weighing carbon fiber, metakaolin and silica fume according to the formula, mixing, putting into a vibration mill, and milling for 20 seconds to form a solid mixture;
(2) weighing solid sodium hydroxide according to the formula amount, putting the solid sodium hydroxide into a beaker, adding ionized water according to the formula amount into the beaker, and completely dissolving the solid sodium hydroxide under stirring to obtain a sodium hydroxide solution;
(3) pouring the solid mixture into a sodium hydroxide solution, and fully stirring to form uniform slurry;
(4) and (3) dip-coating the slurry on the surface of the pretreated steel sheet substrate, placing the pretreated steel sheet substrate in a drying oven under a sealed condition, and curing and reacting for 8 hours at 80 ℃ to obtain the carbon fiber inorganic polymer composite electrode.
The following are specific examples given by the inventors.
Example 1:
accurately weighing 2g of solid sodium hydroxide, weighing 8mL of deionized water, and dissolving the solid sodium hydroxide in the deionized water in a beaker to obtain a sodium hydroxide solution;
accurately weighing 6g of metakaolin, 4g of silica fume and 0.6g of carbon fiber, mixing, and then putting into a vibration mill for grinding for 20 s; pouring the mixed powder into a sodium hydroxide solution, stirring by using a glass rod, uniformly mixing, and carrying out chemical reaction to obtain uniform slurry; the slurry was dip-coated on the surface of a pretreated 304 type stainless steel sheet 15mm (length) 15mm (width) 0.2mm (thickness) (see FIG. 1 for the treatment process), the coating thickness was about 100 μm, the sheet was placed in a dry box under a sealed condition and cured at 80 ℃ for 8 hours to obtain a Carbon Fiber Inorganic polymer Composite Electrode (abbreviated as CFICE; the amount of Carbon Fiber used was 0.6g, and designated as 6CFICE), and the photograph of the Carbon Fiber Inorganic polymer Composite Electrode was as shown in FIG. 2.
The XRD diffraction patterns of the starting materials (silica fume and metakaolin mixture) and the 6CFICE sample are shown in FIG. 3.
Example 2:
all the procedures were the same as in example 1 except that the mass of the Carbon Fiber used was 0.4g, and a Carbon Fiber Inorganic polymer Composite Electrode (Carbon Fiber Inorganic-polymer Composite Electrode, abbreviated as: CFICE; Carbon Fiber amount 0.4g, designated as: 4CFICE) was obtained.
Example 3:
all the procedures were the same as in example 1 except that the mass of the Carbon Fiber used was 0.2g, and a Carbon Fiber Inorganic polymer Composite Electrode (Carbon Fiber Inorganic-polymer Composite Electrode, abbreviated as: CFICE; Carbon Fiber amount 0.2g, designated as: 2CFICE) was obtained; the XRD diffraction pattern of the 2CFICE sample is shown in fig. 3.
Example 4:
the carbon fiber inorganic polymer composite electrode (hereinafter referred to as 6CFICE) obtained in example 1 was connected to the positive electrode of a DC stabilized voltage power supply to serve as the anode of a photoelectrocatalysis device; connecting a steel sheet electrode with the same size as the anode with the negative electrode of a direct current stabilized voltage power supply to be used as the cathode of the photoelectrocatalysis device; putting an anode electrode and a cathode electrode in parallel into 100mL of rhodamine B solution (containing 2mmol/L of sodium persulfate) with the concentration of 5mg/L, wherein the electrode distance is 2 cm; simulation with xenon lampThe sunlight irradiates the anode at a distance of 15 cm; providing 0.8V bias voltage for the electrode by using a direct current stabilized voltage supply, starting timing, taking part of reaction solution in a cuvette every 3min, and measuring the maximum absorption wavelength (lambda) of the rhodamine B dye by using an ultraviolet-visible spectrophotometermax554nm), after the absorbance is measured, the reaction solution in the cuvette is put into the reaction system again, and the degradation rate of the rhodamine B dye is calculated by using the following formula (1):
Figure BDA0002288781640000101
as shown in FIG. 4, the photoelectrocatalytic degradation rate of 6CFICE on rhodamine B dye can reach 99.77% at 9 min.
Example 5:
the carbon fiber inorganic polymer composite electrode (hereinafter referred to as 4CFICE) obtained in example 2 and the positive electrode of a direct current stabilized voltage power supply are connected to be used as the anode of a photoelectrocatalysis device; connecting a steel sheet electrode with the same size as the anode with the negative electrode of a direct current stabilized voltage power supply to be used as the cathode of the photoelectrocatalysis device; the remaining steps were the same as in example 4, and the degradation rate of rhodamine B dye was calculated using formula (1) in example 4.
As shown in FIG. 4, the photoelectrocatalytic degradation rate of 4CFICE on rhodamine B dye can reach 99.76% at 12 min.
Example 6:
the carbon fiber inorganic polymer composite electrode (hereinafter referred to as 2CFICE) obtained in example 3 was connected to the positive electrode of a DC stabilized voltage power supply to serve as the anode of a photoelectrocatalysis device; connecting a steel sheet electrode with the same size as the anode with the negative electrode of a direct current stabilized voltage power supply to be used as the cathode of the photoelectrocatalysis device; the remaining steps were the same as in example 4, and the degradation rate of rhodamine B dye was calculated using formula (1) in example 4.
As shown in FIG. 4, the photoelectrocatalytic degradation rate of 2CFGE on rhodamine B dye can reach 99.46% at 18 min.
Comparative experimental examples are given below:
comparative experimental example 1:
accurately weighing 2g of solid sodium hydroxide, weighing 9mL of deionized water, and dissolving the solid sodium hydroxide in the deionized water in a beaker to obtain a sodium hydroxide solution; accurately weighing 6g of metakaolin, 4g of silica fume and 1.0g of carbon fiber, mixing, placing in a vibration mill, grinding for 20s, pouring the mixed powder into a sodium hydroxide solution, stirring and mixing uniformly by using a glass rod, and carrying out chemical reaction to obtain uniform slurry; the slurry is coated on the surface of a pretreated 304 type stainless steel sheet (the treatment process is shown in figure 1) with the thickness of about 100 mu m, the surface is soaked and coated with the slurry, the thickness of the coating is 15mm (length) multiplied by 15mm (width) multiplied by 0.2mm (thickness), the coating is placed in a drying oven under the sealing condition, the curing reaction is carried out for 8 hours at the temperature of 80 ℃, and the prepared carbon fiber inorganic polymer composite electrode surface coating has cracks and is easy to fall off.
Comparative experiment example 2:
accurately weighing 2g of solid sodium hydroxide, weighing 8mL of deionized water, and dissolving the solid sodium hydroxide in the deionized water in a beaker to obtain a sodium hydroxide solution; accurately weighing 10g of metakaolin, and putting the metakaolin in a vibration mill for grinding for 20 s; pouring the ground powder into a sodium hydroxide solution, stirring by using a glass rod, uniformly mixing, and carrying out chemical reaction to obtain uniform slurry; the slurry is coated on the surface of a pretreated 304 type stainless steel sheet (the treatment process is shown in figure 1) with the thickness of about 100 mu m, the surface is soaked and coated with the slurry, the thickness of the coating is 15mm (length) multiplied by 15mm (width) multiplied by 0.2mm (thickness), the coating is placed in a drying oven under the sealing condition, the curing reaction is carried out for 8 hours at the temperature of 80 ℃, and the prepared inorganic polymer composite electrode has low surface coating strength and cracks.
Comparative experiment example 3:
accurately weighing 2g of solid sodium hydroxide, weighing 8mL of deionized water, and dissolving the solid sodium hydroxide in the deionized water in a beaker to obtain a sodium hydroxide solution; accurately weighing 6g of metakaolin, 4g of silica fume and 0.2g of carbon fiber, and placing in a vibration mill for grinding for 20 s; pouring the mixed powder into a sodium hydroxide solution, stirring by using a glass rod, uniformly mixing, and carrying out chemical reaction to obtain uniform slurry; the slurry is dipped and coated on the surface of a pretreated 304 type stainless steel sheet with the thickness of 15mm (length) multiplied by 15mm (width) multiplied by 0.2mm (thickness) (the treatment process is shown in figure 1), the coating thickness is about 100 mu m, the sheet is placed in a drying box under the condition of no sealing, and the sheet is cured and reacted for 8 hours at the temperature of 80 ℃, so that the surface coating of the prepared carbon fiber inorganic polymer composite electrode has a plurality of cracks, and the coating has the phenomenon of large-area falling off.

Claims (6)

1. The preparation method of the carbon fiber inorganic polymer composite electrode is characterized by comprising the following steps of: 6: 4: 2: and 8, stirring and mixing, uniformly dip-coating on the surface of the pretreated stainless steel substrate, drying, and curing to obtain the carbon fiber inorganic polymer composite electrode.
2. The method according to claim 1, comprising in particular the steps of:
(1) weighing carbon fiber, metakaolin and silica fume according to the formula, mixing, putting into a vibration mill, and milling for 20 seconds to form a solid mixture;
(2) weighing solid sodium hydroxide according to the formula amount, putting the solid sodium hydroxide into a beaker, adding ionized water according to the formula amount into the beaker, and completely dissolving the solid sodium hydroxide under stirring to obtain a sodium hydroxide solution;
(3) pouring the solid mixture into a sodium hydroxide solution, and fully stirring to form uniform slurry;
(4) and (3) dip-coating the slurry on the surface of the pretreated steel sheet substrate, placing the pretreated steel sheet substrate in a drying oven under a sealed condition, and curing and reacting for 8 hours at 80 ℃ to obtain the carbon fiber inorganic polymer composite electrode.
3. The method according to claim 1, wherein the steel sheet is pretreated by polishing the surface of the steel sheet with sand paper, then placing the steel sheet in a sodium hydroxide solution with the mass fraction of 40%, performing a water bath reaction at 80 ℃ for 1h under magnetic stirring, taking out and washing with deionized water, then placing the steel sheet in an oxalic acid solution with the mass fraction of 10%, performing a water bath reaction at 95 ℃ for 30min under magnetic stirring, taking out and washing with deionized water and drying, and placing in absolute ethyl alcohol for storage.
4. A carbon fiber inorganic polymer composite electrode prepared by the method of any one of claims 1 to 3.
5. The use of the carbon fiber inorganic polymer composite electrode as claimed in any one of claims 1 to 4 for photoelectrocatalytic degradation of rhodamine B organic dye wastewater.
6. The use according to claim 5, comprising in particular the following steps:
(1) connecting the prepared carbon fiber inorganic polymer composite electrode with the positive electrode of a direct current stabilized power supply to be used as the anode of a photoelectric catalytic device, and connecting the pretreated steel sheet electrode with the negative electrode of the direct current stabilized power supply to be used as the cathode of the photoelectric catalytic device;
(2) the initial concentration C is prepared by a volumetric flask0Adding a certain amount of sodium persulfate into the rhodamine B dye aqueous solution; using UV-visible spectrophotometer at lambdamaxInitial absorbance a was measured at 554nm0
(3) Placing the anode and the cathode in parallel in a container with a certain volume and concentration of C0In the rhodamine B dye aqueous solution, a certain bias voltage is applied to an electrode, a xenon lamp is used for simulating sunlight to irradiate for a certain time at room temperature, the reaction solution is taken out and put into a cuvette, and an ultraviolet-visible spectrophotometer is used for measuring the color temperature of the rhodamine B dye aqueous solution at lambdamaxAbsorbance A at time t was measured at 554nmtAnd time t rhodamine B dye concentration Ct
(4) After the absorbance is measured, all the reaction liquid is put into the reactor again;
(5) and (5) repeating the step (3) and the step (4) until the absorbance of the rhodamine B dye aqueous solution does not change along with the change of time any more, and calculating the degradation rate of the rhodamine B dye by adopting the following formula:
Figure FDA0002288781630000021
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Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101157535A (en) * 2007-08-28 2008-04-09 东南大学 Short fibre reinforcing inorganic silicon-aluminum polymer composite material
CN101182152A (en) * 2007-11-12 2008-05-21 哈尔滨工业大学 Method for preparing carbon fiber reinforced inorganic polymer based composite material
CN102219279A (en) * 2011-04-13 2011-10-19 同济大学 Visible light catalytic degradation method of organic pollutants based on TiO2/carbon aerogel electrode
CN104529370A (en) * 2015-01-14 2015-04-22 哈尔滨工业大学 Carbon fiber felt reinforcement inorganic polymer matrix composite and preparation method thereof
US20160023951A1 (en) * 2013-01-07 2016-01-28 Vince Alessi Thermoset ceramic compositions, inorganic polymer coatings, inorganic polymer mold tooling, inorganic polymer hydraulic fracking proppants, methods of preparation and applications therefore
CN106165165A (en) * 2014-02-10 2016-11-23 纽卡斯尔创新有限公司 Electrode of adulterant doping and application thereof
JP2017188334A (en) * 2016-04-06 2017-10-12 凸版印刷株式会社 Electrode for nonaqueous electrolyte secondary battery, and nonaqueous electrolyte secondary battery

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101157535A (en) * 2007-08-28 2008-04-09 东南大学 Short fibre reinforcing inorganic silicon-aluminum polymer composite material
CN101182152A (en) * 2007-11-12 2008-05-21 哈尔滨工业大学 Method for preparing carbon fiber reinforced inorganic polymer based composite material
CN102219279A (en) * 2011-04-13 2011-10-19 同济大学 Visible light catalytic degradation method of organic pollutants based on TiO2/carbon aerogel electrode
US20160023951A1 (en) * 2013-01-07 2016-01-28 Vince Alessi Thermoset ceramic compositions, inorganic polymer coatings, inorganic polymer mold tooling, inorganic polymer hydraulic fracking proppants, methods of preparation and applications therefore
CN106165165A (en) * 2014-02-10 2016-11-23 纽卡斯尔创新有限公司 Electrode of adulterant doping and application thereof
CN104529370A (en) * 2015-01-14 2015-04-22 哈尔滨工业大学 Carbon fiber felt reinforcement inorganic polymer matrix composite and preparation method thereof
JP2017188334A (en) * 2016-04-06 2017-10-12 凸版印刷株式会社 Electrode for nonaqueous electrolyte secondary battery, and nonaqueous electrolyte secondary battery

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
YAOJUN ZHANG等: "Fly ash-based geopolymer as a novel photocatalyst for degradation of dye from wastewater", 《PARTICUOLOGY》 *
何晓文等: "《水体污染处理新技术及应用》", 31 March 2013 *
娄春华等: "《聚合物结构与性能》", 31 July 2016 *

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