WO2022000364A1 - Biomembrane electrode material based on special-shaped carbon fiber, and preparation method therefor and use thereof - Google Patents

Biomembrane electrode material based on special-shaped carbon fiber, and preparation method therefor and use thereof Download PDF

Info

Publication number
WO2022000364A1
WO2022000364A1 PCT/CN2020/099699 CN2020099699W WO2022000364A1 WO 2022000364 A1 WO2022000364 A1 WO 2022000364A1 CN 2020099699 W CN2020099699 W CN 2020099699W WO 2022000364 A1 WO2022000364 A1 WO 2022000364A1
Authority
WO
WIPO (PCT)
Prior art keywords
carbon fiber
special
electrode
shaped
electrode material
Prior art date
Application number
PCT/CN2020/099699
Other languages
French (fr)
Chinese (zh)
Inventor
罗鸿斌
Original Assignee
东莞理工学院
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 东莞理工学院 filed Critical 东莞理工学院
Priority to PCT/CN2020/099699 priority Critical patent/WO2022000364A1/en
Publication of WO2022000364A1 publication Critical patent/WO2022000364A1/en

Links

Images

Classifications

    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M8/00Fuel cells; Manufacture thereof
    • H01M8/16Biochemical fuel cells, i.e. cells in which microorganisms function as catalysts
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/30Hydrogen technology
    • Y02E60/50Fuel cells

Definitions

  • the present invention relates to the technical field of biological electrode material and wastewater treatment, and relates to a special-shaped carbon fiber-based biological membrane electrode material and a preparation method and application thereof.
  • the traditional methods of water pollution control include physical method, chemical method and biological method, but each method has certain limitations.
  • the physical method has complex equipment requirements, high cost, and it is difficult to meet the discharge standard after one treatment; the chemical method is sometimes incomplete in treatment of pollutants, and there is a danger of secondary pollution; the biological method is limited by the type of target pollutants when it acts The effect on refractory pollutants is not obvious.
  • the biofilm electrode method combines chemical and biological methods, which can effectively deal with pollutants that are difficult to biodegrade or incompletely treated by electrolysis, and become the preferred method for the treatment of refractory organic polluted wastewater.
  • the advantage is that the close adsorption of microorganisms on the electrode surface weakens the direct toxic effect of harmful substances on microorganisms, and improves the safety of system operation.
  • a good conductivity-mass transfer relationship is formed between the biofilm and the substrate electrode, and the additional electrode potential has a certain influence on the enzyme catalysis, which may promote the oxidation or reduction of the target, thereby improving the degradation ability of the system.
  • the process of treating organic pollutants in water by the biofilm electrode method is very complicated, and the treatment effect is closely related to the biofilm electrode material and solution composition, and the direct electro-oxidation and indirect electro-oxidation reactions often occur at the same time.
  • the biofilm electrode material uses immobilization technology to immobilize microorganisms on the surface of the electrode to form a layer of biofilm.
  • the biofilm is an electricity-generating microbial film, which oxidizes organic matter under anaerobic conditions and generates electric current, and at the same time obtains energy for growth and reproduction in the process of electron transfer.
  • the advantage is that the close adsorption of microorganisms on the electrode surface weakens the direct toxic effect of harmful substances on microorganisms, and improves the safety of system operation.
  • a good conductivity-mass transfer relationship is formed between the biofilm and the substrate electrode, and the additional electrode potential has a certain influence on the enzyme catalysis, which may promote the oxidation or reduction of the target, thereby improving the degradation ability of the system. Therefore, the preparation of biofilm electrode materials with high specific surface area and high electronic conductivity is the key to improve the efficiency of microbial fuel cells (MFC) in the treatment of organic wastewater.
  • MFC microbial fuel cells
  • graphene has been used to modify MFC electrodes due to its large specific surface area and excellent electrical conductivity.
  • graphene oxide can be reduced to graphene by microorganisms with extracellular electron transfer function under anaerobic conditions, and there is direct electron transfer on the surface of extracellular electron transfer bacteria (electrogenic bacteria) and graphene oxide.
  • the cells of the electrogenic bacteria can be captured by the graphene oxide nanosheets.
  • the graphene oxide nanosheets act as a net to capture the electrogenic bacteria.
  • the graphene oxide nanosheets are reduced to graphene and self-assemble with the electrogenic bacteria. into graphene/electricity-generating bacteria net.
  • This structure enables a large number of electrogenic bacteria to enter the formed graphene/biofilm matrix and form multiple conductive pathways, thereby facilitating electron transfer between the electrogenic bacteria and the electrodes.
  • an important aspect that cannot be ignored is the antibacterial properties of graphene.
  • Graphene will affect the growth of anode biofilm in the early stage, and will reduce the electrochemical activity and metabolic activity of the surface biofilm. When the biofilm matures After that, the contact surface between graphene and bacteria decreased, the adhesion of electrogenic bacteria on the surface of graphene biocathode increased, the electron transfer rate increased, and the biofilm metabolism and electrochemical performance were improved.
  • the present invention constructs a nano-conductive network by structurally designing the electrode substrate of the biofilm electrode material, and then sequentially modifying the surface of the electrode substrate with graphene and polypyrrole nanowires, which significantly improves the specific surface area and the specific surface area of the biofilm electrode material. current density.
  • the purpose of the present invention is to provide a special-shaped carbon fiber-based biofilm electrode material and its preparation method and application, so as to obtain a biofilm electrode material with high circuit density and high organic wastewater degradation rate.
  • a special-shaped carbon fiber-based biofilm electrode material comprising a special-shaped cross-section carbon fiber fabric electrode substrate and a biofilm supported on the electrode substrate
  • the special-shaped cross-section carbon fiber fabric electrode substrate comprises a special-shaped cross-section carbon fiber fabric and its surface and Graphene and polypyrrole are loaded between the carbon fiber voids, and the polypyrrole is loaded on the surface of the graphene to form polypyrrole nanowires, forming a three-dimensional nano-conductive network structure.
  • the special-shaped cross-section is a Y-shaped cross-section or a star-shaped cross-section.
  • the carbon fiber fabric is carbon cloth or carbon felt made of polyacrylonitrile carbon fiber.
  • the thickness of the carbon fiber fabric is 0.05 mm to 1 mm, and the spacing of the polyacrylonitrile carbon fibers is less than 100 ⁇ m.
  • biofilm is an electroactive microbial film.
  • a preparation method of the above-mentioned special-shaped carbon fiber-based biofilm electrode material comprising the following steps:
  • the special-shaped cross-section carbon fiber is made into a carbon fiber fabric with a thickness of 0.05mm to 1mm;
  • step S2 after the carbon fiber fabric described in step S1 is impregnated and adsorbed in the graphene oxide solution, suction filtration is performed, and then the carbon fiber fabric loaded with graphene is obtained by reduction;
  • the graphene-loaded carbon fiber fabric obtained in step S2 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is soaked in an electrolyte containing pyrrole monomer and NaClO 4 .
  • polypyrrole nanowires are grown on the surface of graphene-loaded carbon fiber fabric by electrochemical deposition process to obtain a special-shaped cross-section carbon fiber electrode substrate;
  • step S4 The special-shaped cross-section carbon fiber electrode substrate obtained in step S3 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is immersed in an electrolyte inoculated with electroactive microorganisms. , culturing with direct current to obtain the special-shaped carbon fiber-based biofilm electrode material;
  • the electrolyte contains carbon source, PBS buffer, vitamins and trace elements.
  • step S3 the concentration of the pyrrole monomer is 50-100 mg/L, and the concentration of the NaClO 4 is 20-40 g/L.
  • the carbon source is organic matter in the organic wastewater to be treated, and the concentration of the organic matter is 50-120 mg/L.
  • step S4 the current of the direct current is 3-8 mA.
  • the special-shaped carbon fiber-based biofilm electrode material is used for biofilm electrolysis of organic wastewater deal with.
  • the special-shaped carbon fiber-based biofilm electrode material and its preparation method and application provided by the present invention have the following beneficial effects:
  • a special-shaped cross-section carbon fiber fabric is selected as the electrode load matrix. , which can increase the specific surface area of the carbon fiber fabric.
  • the special-shaped carbon fiber is made into a carbon fiber fabric with a certain thickness, the special-shaped carbon fibers are arranged together, and the gaps of the special-shaped cross-section are connected with each other to form a gap network structure.
  • Graphene is loaded on the surface and voids of the carbon fibers, and the load is significantly increased, and the graphene filled in the voids of the carbon fibers is distributed in a two-dimensional line along the length of the carbon fibers, and then connected by the graphene loaded on the surface of the carbon fibers to form a three-dimensional conductive network structure. Then, polypyrrole is grown in situ on the surface of graphene to form a three-dimensional nano-conductive network structure composed of polypyrrole nanowires, and finally a biofilm is loaded on its surface, which can prevent the graphene from directly contacting the biofilm and overcome the antibacterial effect of graphene. Problems leading to reduced biofilm performance.
  • the preparation method of the special-shaped carbon fiber-based biofilm electrode material provided by the present invention can obtain the special-shaped cross-section carbon fiber fabric electrode substrate with different graphene and polypyrrole loadings by controlling the thickness of the carbon fiber and the spacing between the carbon fibers, thereby The electrical conductivity of the electrode substrate is regulated.
  • suction filtration is performed to improve the loading capacity and loading fastness of graphene oxide, and reduce the vacancies formed by unloaded graphene and polypyrrole, thereby improving the electron transfer rate of the electrode material.
  • the special-shaped carbon fiber-based biofilm electrode material provided by the present invention can be used for the treatment of organic wastewater, and has the advantages of high current density, high treatment efficiency and high electrical degradation rate.
  • Fig. 1 is the cross-sectional schematic diagram of the special-shaped carbon fiber of the special-shaped carbon fiber-based biofilm electrode material provided by the present invention
  • FIG. 2 is a schematic cross-sectional view of a special-shaped cross-section carbon fiber fabric of a special-shaped carbon fiber-based biofilm electrode material provided by the present invention
  • FIG. 3 is a schematic cross-sectional view of a carbon fiber fabric electrode substrate with a special-shaped cross-section of the special-shaped carbon fiber-based biofilm electrode material provided by the present invention.
  • the special-shaped carbon fiber-based biofilm electrode material provided by the present invention includes a special-shaped cross-section carbon fiber fabric electrode substrate and a biofilm supported on the electrode substrate.
  • the special-shaped cross-section carbon fiber fabric electrode substrate includes a special-shaped cross-section carbon fiber fabric and its Graphene and polypyrrole are loaded between the surface and the carbon fiber voids, and the polypyrrole is loaded on the graphene surface to form polypyrrole nanowires, forming a three-dimensional nano-conductive network structure.
  • the special-shaped cross-section carbon fiber fabric is selected as the electrode load matrix.
  • the irregular cross-section carbon fibers are arranged irregularly, so that there are more gaps between the special-shaped cross-section carbon fibers, which can increase the specific surface area of the carbon fiber fabric.
  • Graphene is loaded on the surface and voids of the carbon fibers, and the load is significantly increased, and the graphene filled in the voids of the carbon fibers is distributed in a two-dimensional line along the length of the carbon fibers, and then connected by the graphene loaded on the surface of the carbon fibers to form a three-dimensional conductive network structure.
  • polypyrrole is grown in situ on the surface of graphene to form a three-dimensional nano-conductive network structure composed of polypyrrole nanowires, and finally a biofilm is loaded on its surface, which can prevent the graphene from directly contacting the biofilm and overcome the antibacterial effect of graphene. Problems leading to reduced biofilm performance.
  • the special-shaped cross-section is a Y-shaped cross-section or a star-shaped cross-section.
  • each carbon fiber with a Y-shaped cross-section or a star-shaped cross-section has more voids due to the bifurcated structure.
  • Figures 2 and 3 that when carbon fibers are made into carbon fiber fabrics with a certain thickness, the carbon fibers are arranged together, and the voids of the special-shaped cross-sections are connected to each other to form a void network structure. After the graphene and polypyrrole are loaded into the voids, a three-dimensional conductive network structure is formed.
  • the carbon fiber fabric is carbon cloth or carbon felt made of polyacrylonitrile carbon fiber.
  • the thickness of the carbon fiber fabric is 0.05 mm ⁇ 1 mm, and the spacing of the polyacrylonitrile carbon fibers is less than 100 ⁇ m.
  • the spacing of carbon fibers refers to the distance between any two adjacent carbon fibers when carbon fibers are made into fabrics, and the spacing of carbon fibers is too large, which is not conducive to the formation of a connected conductive network.
  • the biofilm is an electroactive microbial film.
  • an electroactive microbial film Such as aerobic bacteria or anaerobic bacteria microbial membrane, according to the type of organic matter in the organic wastewater to be treated, different microbial colonies are inoculated to realize the microbial electrochemical degradation treatment of organic wastewater.
  • a preparation method of the above-mentioned special-shaped carbon fiber-based biofilm electrode material comprising the following steps:
  • the special-shaped cross-section carbon fiber is made into a carbon fiber fabric with a thickness of 0.05 mm to 1 mm.
  • step S2 after soaking and adsorbing the carbon fiber fabric described in step S1 in the graphene oxide solution for 1 ⁇ 4h, carry out suction filtration, and then reduce to obtain the carbon fiber fabric loaded with graphene;
  • Graphene oxide is reduced to graphene by ultraviolet irradiation reduction method, electrochemical reduction method, etc.; after impregnation and adsorption, graphene oxide is adsorbed on the surface of carbon fiber fabric and between carbon fiber gaps, and then through suction filtration, the loading capacity of graphene oxide is increased and load fastness, overcoming the problem of reduced electron transport rate of electrode materials due to vacancies formed by unloading.
  • the graphene-loaded carbon fiber fabric obtained in step S2 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is soaked in an electrolyte containing pyrrole monomer and NaClO 4 .
  • polypyrrole nanowires were grown on the surface of graphene-loaded carbon fiber fabric by electrochemical deposition process to obtain a special-shaped cross-section carbon fiber electrode substrate;
  • the concentration of the pyrrole monomer is 50-100 mg/L, and the concentration of the NaClO 4 is 20-40 g/L.
  • step S4 The special-shaped cross-section carbon fiber electrode substrate obtained in step S3 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is immersed in an electrolyte inoculated with electroactive microorganisms. , culturing with direct current to obtain the special-shaped carbon fiber-based biofilm electrode material.
  • the electrolyte contains carbon source, PBS buffer, vitamins and trace elements.
  • the carbon source is organic matter in the organic wastewater to be treated, such as phenol, fluorine-containing organic matter, nitrogen-containing organic matter, and phosphorus-containing organic matter.
  • concentration of the organic matter is 50-120 mg/L.
  • the formation mechanism of the biofilm is as follows: the inoculated electroactive microorganisms first adhere to the surface of the carbon fiber electrode substrate with special-shaped cross-section to form microcolonies and fuse into the base layer of the biofilm; at the same time, extracellular polymers are produced and released, followed by the formation of microcolonies. With the extension of the culture time, the structure of the biofilm became more complicated and developed into a mature biofilm.
  • the biofilm on the surface is mainly composed of microbial cells, extracellular polymers and inorganic ions in the water system, and the water content in the film is more than 95%, forming a porous structure state.
  • the application principle of biofilm electrodes is to electrically stimulate microorganisms that already have the ability to remove certain pollutants, increase their metabolism or consume pollutants, and use the charge transfer between the electrode substrate and the pollutants. Double degradation.
  • step S4 the current of the direct current is 3-8 mA.
  • the special-shaped carbon fiber-based biofilm electrode material is used for biofilm electrolysis of organic wastewater deal with.
  • the treatment method is as follows: using the special-shaped carbon fiber-based biofilm electrode material as the working electrode of the microbial fuel cell, preparing the organic wastewater to be treated into an electrolyte, and performing electrolytic treatment.
  • the basic processes of biological metabolism of organic pollutants include access to substrates, adsorption of solid substrates, secretion of extracellular enzymes, absorption of permeable substances and intracellular metabolism.
  • Microorganisms first grow close to a certain substrate, and then adsorb on the surface of the substrate. When faced with macromolecular multimeric compounds, microorganisms secrete extracellular enzymes to hydrolyze part of macromolecules into soluble products of small molecules, which are easily degraded and mineralized by other microorganisms. Small molecule products enter cells through the cell membrane through four modes: simple diffusion, facilitated diffusion, active transport and group translocation, and are degraded through peripheral metabolic pathways.
  • a special-shaped carbon fiber-based biofilm electrode material comprising a Y-shaped cross-section PAN carbon fiber fabric electrode substrate and a biofilm supported on the electrode substrate, the Y-shaped cross-section PAN carbon fiber fabric electrode substrate includes a Y-shaped cross-section PAN Graphene and polypyrrole supported between the carbon fiber fabric and its surface and carbon fiber voids, the polypyrrole is supported on the graphene surface to form polypyrrole nanowires, and constitute a three-dimensional nano-conductive network structure.
  • the preparation method is as follows:
  • the Y-shaped cross-section PAN carbon fiber is made into a carbon fiber cloth with a thickness of 0.1 mm and a carbon fiber spacing of 80-100 ⁇ m;
  • step S2 after the carbon fiber cloth described in step S1 is soaked and adsorbed in the graphene oxide solution for 2h, suction filtration is performed, after the soaking and adsorption, the graphene oxide is adsorbed on the surface of the carbon fiber cloth and between the carbon fiber gaps, and then by suction filtration, to improve oxidation
  • the loading amount and loading fastness of graphene can overcome the problem that the electron transport rate of the electrode material is reduced due to the vacancies formed by unloading, and then the graphene-loaded carbon fiber cloth is obtained by electrochemical reduction method;
  • the graphene-loaded carbon fiber cloth obtained in step S2 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, and the concentration of immersed in the pyrrole monomer is 65mg/L, In an electrolyte with a concentration of NaClO 4 of 30 g/L, under a constant voltage of 0.8 V, polypyrrole nanowires were grown on the surface of the graphene-loaded carbon fiber fabric by an electrochemical deposition process to obtain a special-shaped cross-section carbon fiber electrode substrate; The electrochemical deposition process helps to form polypyrrole nanowires and a uniform conductive network structure on the surface of graphene, thereby improving the electron transfer rate and current density of the electrode material;
  • the Y-shaped cross-section PAN electrode substrate obtained in step S3 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system.
  • the direct current of 5mA is used for cultivation to obtain a Y-shaped cross-section PAN-based biofilm electrode material; the electrolyte contains 100mg/L carbon source, 50mmol/L PBS buffer, 10ml/L vitamins and trace amounts. element.
  • a special-shaped carbon fiber-based biofilm electrode material compared with Example 1, the difference is that the PAN carbon fiber fabric is a circular cross-section PAN carbon fiber, the other is roughly the same as Example 1, and will not be repeated here.
  • a special-shaped carbon fiber-based biofilm electrode material compared with Example 1, is different in that it includes a Y-shaped cross-section PAN carbon fiber fabric and a biofilm loaded on the carbon fiber fabric, that is, unloaded graphene and polypyrrole, prepared
  • the method does not include steps S2 and S3, and the others are substantially the same as those in Embodiment 1, which will not be repeated here.
  • a special-shaped carbon fiber-based biofilm electrode material compared with Example 1, the difference is that the Y-shaped cross-section PAN carbon fiber fabric electrode substrate comprises a Y-shaped cross-section PAN carbon fiber fabric and its surface and the carbon fiber voids between Supported graphene, i.e. unsupported polypyrrole. Others are substantially the same as those in Embodiment 1, and are not repeated here.
  • a special-shaped carbon fiber-based biofilm electrode material compared with Example 1, the difference is that the Y-shaped cross-section PAN carbon fiber fabric electrode substrate comprises a Y-shaped cross-section PAN carbon fiber fabric and the surface between the surface and the carbon fiber voids Supported polypyrrole, i.e. unsupported graphene. Others are substantially the same as those in Embodiment 1, and are not repeated here.
  • Example 1 Compared with Example 1, the special-shaped carbon fiber-based biofilm electrode materials provided in Examples 2 to 4 and Comparative Example 5 are different in that the thickness of the Y-shaped cross-section PAN carbon fiber and the carbon fiber gap are shown in Table 1. Others are substantially the same as those in Embodiment 1, and are not repeated here.
  • Application Examples 1 to 4 and Application Comparative Examples 1 to 5 are respectively using the Y-shaped carbon fiber-based biofilm electrode materials prepared in Examples 1 to 4 and Comparative Examples 1 to 5 for the treatment of organic wastewater containing phenol.
  • the treatment methods are as follows: The Y-shaped carbon fiber-based biofilm electrode material is used as the working electrode of the microbial fuel cell, and the organic wastewater containing phenol is prepared into an electrolyte, and electrolytic treatment is performed.
  • the phenol concentration in the organic wastewater is 1500mg/L, and the COD content is 2500mg /L.
  • the Y-shaped carbon fiber-based biofilm electrode material prepared by the preparation method provided by the present invention is used for bioelectric degradation treatment of phenolic organic wastewater, the removal rate of phenol is as high as 99%, and the conversion rate of COD is as high as 95% above.
  • the carbon fiber has a circular cross-section, the current density, phenol removal rate and COD conversion rate are significantly reduced, just because the carbon fiber with a circular cross-section is densely arranged, the carbon fiber has fewer voids, and the specific surface area is reduced, resulting in graphene and polymer The loading of pyrrole is reduced, and the three-dimensional conductive network structure cannot be formed through voids and surface loading.

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Biochemistry (AREA)
  • Microbiology (AREA)
  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Sustainable Development (AREA)
  • Sustainable Energy (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

Provided are a biomembrane electrode material based on special-shaped carbon fiber, and a preparation method therefor and the use thereof. The biomembrane electrode material comprises a special-shaped cross-section carbon fiber fabric electrode substrate and a biomembrane loaded on the electrode substrate. The special-shaped cross-section carbon fiber fabric electrode substrate comprises a special-shaped cross-section carbon fiber fabric, and graphene and polypyrrole loaded on the surface of the fabric and in voids of carbon fibers, wherein the polypyrrole is loaded on the surface of the graphene and forms polypyrrole nanowires, which form a three-dimensional nano-conductive network structure. The use of the special-shaped cross-section carbon fiber fabric as an electrode loading matrix can increase the specific surface area of the carbon fiber fabric. In addition, the voids of the special-shaped cross-section are in communication with each other, such that a void network structure is formed. When graphene and polypyrrole are loaded on the surface and in the voids of the fabric, a three-dimensional conductive network structure can be formed, and the problem of a reduced biomembrane performance caused by the antimicrobial effect of graphene can be overcome. The use thereof in organic wastewater treatment has the characteristics of a high current density and a high degradation rate.

Description

一种异形碳纤维基生物膜电极材料及其制备方法和应用A special-shaped carbon fiber-based biofilm electrode material and its preparation method and application 技术领域technical field
本发明生物电极材料及废水处理技术领域,涉及一种异形碳纤维基生物膜电极材料及其制备方法和应用。The present invention relates to the technical field of biological electrode material and wastewater treatment, and relates to a special-shaped carbon fiber-based biological membrane electrode material and a preparation method and application thereof.
背景技术Background technique
传统水环境污染物治理的方法包括物理法、化学法和生物法,但每一种方法都存在一定的局限性。物理法设备要求复杂,成本较高,且难以经一次处理后达到排放标准;化学法处理污染物有时不彻底,且有造成二次污染的危险;生物法在作用时受目标污染物种类限制,对于难生物降解的污染物作用效果不明显。生物膜电极法将化学法和生物法相结合,可有效处理难生物降解或电解处理不彻底的污染物,成为处理难降解有机污染废水的优选方法。The traditional methods of water pollution control include physical method, chemical method and biological method, but each method has certain limitations. The physical method has complex equipment requirements, high cost, and it is difficult to meet the discharge standard after one treatment; the chemical method is sometimes incomplete in treatment of pollutants, and there is a danger of secondary pollution; the biological method is limited by the type of target pollutants when it acts The effect on refractory pollutants is not obvious. The biofilm electrode method combines chemical and biological methods, which can effectively deal with pollutants that are difficult to biodegrade or incompletely treated by electrolysis, and become the preferred method for the treatment of refractory organic polluted wastewater.
其优势在于微生物在电极表面的紧密吸附削弱了有害物质对微生物的直接毒害作用,使体系运行的安全性提高。此外,生物膜与基体电极间形成了良好的电导-传质关系,外加电极电位对酶催化造成一定影响,可能促进目标物的氧化或还原,进而提高体系的降解能力。The advantage is that the close adsorption of microorganisms on the electrode surface weakens the direct toxic effect of harmful substances on microorganisms, and improves the safety of system operation. In addition, a good conductivity-mass transfer relationship is formed between the biofilm and the substrate electrode, and the additional electrode potential has a certain influence on the enzyme catalysis, which may promote the oxidation or reduction of the target, thereby improving the degradation ability of the system.
一般情况下,生物膜电极法处理水中有机污染物的过程非常复杂,处理效果与生物膜电极材料、溶液组成等关系密切,直接电氧化和间接电氧化反应常同时发生。其中,生物膜电极材料是采用固定化技术将微生物固定在电极表面,形成一层生物膜。该生物膜为产电微生物膜,它在厌氧条件下氧化有机物并产生电流,同时在电子传递过程中获得能量以供生长繁殖。其优势在于微生物在电极表面的紧密吸附削弱了有害物质对微生物的直接毒害作用,使体系运行的安全性提高。此外,生物膜与基体电极间形成了良好的电导-传质关系,外加电极电位对酶催化造成一定影响,可能促进目标物的氧化或还原,进而提高体系的降解能力。因此制备高比表面积和高电子传导性能 的生物膜电极材料是提高微生物燃料电池(MFC)处理有机废水效率的关键。In general, the process of treating organic pollutants in water by the biofilm electrode method is very complicated, and the treatment effect is closely related to the biofilm electrode material and solution composition, and the direct electro-oxidation and indirect electro-oxidation reactions often occur at the same time. Among them, the biofilm electrode material uses immobilization technology to immobilize microorganisms on the surface of the electrode to form a layer of biofilm. The biofilm is an electricity-generating microbial film, which oxidizes organic matter under anaerobic conditions and generates electric current, and at the same time obtains energy for growth and reproduction in the process of electron transfer. The advantage is that the close adsorption of microorganisms on the electrode surface weakens the direct toxic effect of harmful substances on microorganisms, and improves the safety of system operation. In addition, a good conductivity-mass transfer relationship is formed between the biofilm and the substrate electrode, and the additional electrode potential has a certain influence on the enzyme catalysis, which may promote the oxidation or reduction of the target, thereby improving the degradation ability of the system. Therefore, the preparation of biofilm electrode materials with high specific surface area and high electronic conductivity is the key to improve the efficiency of microbial fuel cells (MFC) in the treatment of organic wastewater.
近年来,由于石墨烯自身具有的比表面积大和导电性优良的特征,石墨烯已经用来修饰MFC电极。研究表明氧化石墨烯可以在厌氧条件下被具有胞外电子传递功能的微生物还原为石墨烯,且胞外电子传递菌(产电菌)和氧化石墨烯表面存在直接电子传递。产电菌的细胞可以被氧化石墨烯的纳米片捕获,氧化石墨烯纳米片起着网的作用去捕捉产电菌,同时氧化石墨烯纳米片被还原成石墨烯,并与产电菌自组装成石墨烯/产电菌网。这一结构使大量产电菌进入形成的石墨烯/生物膜矩阵,并形成多路导电通路,从而促进产电菌和电极之间的电子转移。但是石墨烯修饰生物电极MFC的研究中一个不可忽略的是石墨烯的抗菌性能,石墨烯会对阳极生物膜生长初期造成影响,会降低表面生物膜的电化学活性和新陈代谢活性,在生物膜成熟后,石墨烯与细菌的接触面降低,石墨烯生物阴极表面的产电菌附着增多,电子传递速率增大,生物膜代谢和电化学性能得以提升。In recent years, graphene has been used to modify MFC electrodes due to its large specific surface area and excellent electrical conductivity. Studies have shown that graphene oxide can be reduced to graphene by microorganisms with extracellular electron transfer function under anaerobic conditions, and there is direct electron transfer on the surface of extracellular electron transfer bacteria (electrogenic bacteria) and graphene oxide. The cells of the electrogenic bacteria can be captured by the graphene oxide nanosheets. The graphene oxide nanosheets act as a net to capture the electrogenic bacteria. At the same time, the graphene oxide nanosheets are reduced to graphene and self-assemble with the electrogenic bacteria. into graphene/electricity-generating bacteria net. This structure enables a large number of electrogenic bacteria to enter the formed graphene/biofilm matrix and form multiple conductive pathways, thereby facilitating electron transfer between the electrogenic bacteria and the electrodes. However, in the research of graphene-modified bioelectrode MFC, an important aspect that cannot be ignored is the antibacterial properties of graphene. Graphene will affect the growth of anode biofilm in the early stage, and will reduce the electrochemical activity and metabolic activity of the surface biofilm. When the biofilm matures After that, the contact surface between graphene and bacteria decreased, the adhesion of electrogenic bacteria on the surface of graphene biocathode increased, the electron transfer rate increased, and the biofilm metabolism and electrochemical performance were improved.
有鉴于此,本发明通过对生物膜电极材料的电极基材进行结构设计,然后依次在其表面修饰石墨烯和聚吡咯纳米线,构建了纳米导电网络,显著提升生物膜电极材料的比表面积和电流密度。In view of this, the present invention constructs a nano-conductive network by structurally designing the electrode substrate of the biofilm electrode material, and then sequentially modifying the surface of the electrode substrate with graphene and polypyrrole nanowires, which significantly improves the specific surface area and the specific surface area of the biofilm electrode material. current density.
发明内容SUMMARY OF THE INVENTION
针对上述现有技术存在的缺陷,本发明的目的在于提供一种异形碳纤维基生物膜电极材料及其制备方法和应用,从而得到具有高电路密度和高有机废水降解率的生物膜电极材料。In view of the above-mentioned defects in the prior art, the purpose of the present invention is to provide a special-shaped carbon fiber-based biofilm electrode material and its preparation method and application, so as to obtain a biofilm electrode material with high circuit density and high organic wastewater degradation rate.
为实现上述目的,本发明采用的技术方案如下:For achieving the above object, the technical scheme adopted in the present invention is as follows:
一种异形碳纤维基生物膜电极材料,包括异形横截面碳纤维织物电极基材以及负载在电极基材上的生物膜,所述异形横截面碳纤维织物电极基材包括异形横截面碳纤维织物及其表面和碳纤维空隙之间负载的石墨烯和聚吡咯,所述聚吡咯负载于所述石墨烯表面形成聚吡咯纳米线,构成三维纳米导 电网络结构。A special-shaped carbon fiber-based biofilm electrode material, comprising a special-shaped cross-section carbon fiber fabric electrode substrate and a biofilm supported on the electrode substrate, the special-shaped cross-section carbon fiber fabric electrode substrate comprises a special-shaped cross-section carbon fiber fabric and its surface and Graphene and polypyrrole are loaded between the carbon fiber voids, and the polypyrrole is loaded on the surface of the graphene to form polypyrrole nanowires, forming a three-dimensional nano-conductive network structure.
进一步的,所述异形横截面为Y形横截面或星形横截面。Further, the special-shaped cross-section is a Y-shaped cross-section or a star-shaped cross-section.
进一步的,所述碳纤维织物为聚丙烯腈碳纤维制成的碳布或碳毡。Further, the carbon fiber fabric is carbon cloth or carbon felt made of polyacrylonitrile carbon fiber.
进一步的,所述碳纤维织物的厚度为0.05mm~1mm,所述聚丙烯腈碳纤维的间距小于100μm。Further, the thickness of the carbon fiber fabric is 0.05 mm to 1 mm, and the spacing of the polyacrylonitrile carbon fibers is less than 100 μm.
进一步的,所述生物膜为电活性微生物膜。Further, the biofilm is an electroactive microbial film.
一种以上所述的异形碳纤维基生物膜电极材料的制备方法,包括以下步骤:A preparation method of the above-mentioned special-shaped carbon fiber-based biofilm electrode material, comprising the following steps:
S1.将异形横截面碳纤维制成厚度为0.05mm~1mm的碳纤维织物;S1. The special-shaped cross-section carbon fiber is made into a carbon fiber fabric with a thickness of 0.05mm to 1mm;
S2.将步骤S1所述碳纤维织物在氧化石墨烯溶液中浸渍吸附后,进行抽滤,然后还原得到负载石墨烯的碳纤维织物;S2. after the carbon fiber fabric described in step S1 is impregnated and adsorbed in the graphene oxide solution, suction filtration is performed, and then the carbon fiber fabric loaded with graphene is obtained by reduction;
S3.将步骤S2得到的所述负载石墨烯的碳纤维织物作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在包含吡咯单体和NaClO 4的电解液中,通过电化学沉积工艺在负载石墨烯的碳纤维织物表面生长聚吡咯纳米线,得到异形横截面碳纤维电极基材; S3. The graphene-loaded carbon fiber fabric obtained in step S2 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is soaked in an electrolyte containing pyrrole monomer and NaClO 4 . In , polypyrrole nanowires are grown on the surface of graphene-loaded carbon fiber fabric by electrochemical deposition process to obtain a special-shaped cross-section carbon fiber electrode substrate;
S4.将步骤S3得到的所述异形横截面碳纤维电极基材作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在接种有电活性微生物的电解液中,通直流电进行培养,得到所述异形碳纤维基生物膜电极材料;S4. The special-shaped cross-section carbon fiber electrode substrate obtained in step S3 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is immersed in an electrolyte inoculated with electroactive microorganisms. , culturing with direct current to obtain the special-shaped carbon fiber-based biofilm electrode material;
所述电解液中包含碳源、PBS缓冲液、维生素和微量元素。The electrolyte contains carbon source, PBS buffer, vitamins and trace elements.
进一步的,在步骤S3中,所述吡咯单体的浓度为50~100mg/L,所述NaClO 4的浓度为20~40g/L。 Further, in step S3, the concentration of the pyrrole monomer is 50-100 mg/L, and the concentration of the NaClO 4 is 20-40 g/L.
进一步的,在步骤S4中,所述碳源为待处理的有机废水中的有机物,所述有机物的浓度为50~120mg/L。Further, in step S4, the carbon source is organic matter in the organic wastewater to be treated, and the concentration of the organic matter is 50-120 mg/L.
进一步的,在步骤S4中,所述直流电的电流为3~8mA。Further, in step S4, the current of the direct current is 3-8 mA.
一种以上所述的异形碳纤维基生物膜电极材料,或者以上所述的制备方法制备的异形碳纤维基生物膜电极材料的应用,所述异形碳纤维基生物膜电极材料用于有机废水的生物膜电解处理。Application of the above-mentioned special-shaped carbon fiber-based biofilm electrode material, or the application of the special-shaped carbon fiber-based biofilm electrode material prepared by the above-mentioned preparation method, the special-shaped carbon fiber-based biofilm electrode material is used for biofilm electrolysis of organic wastewater deal with.
有益效果beneficial effect
与现有技术相比,本发明提供的异形碳纤维基生物膜电极材料及其制备方法和应用具有如下有益效果:Compared with the prior art, the special-shaped carbon fiber-based biofilm electrode material and its preparation method and application provided by the present invention have the following beneficial effects:
(1)本发明提供的异形碳纤维基生物膜电极材料,选用异形横截面碳纤维织物作为电极负载基体,在异形横截面碳纤维织物中,异形横截面碳纤维不规则排列,异形横截面碳纤维的空隙较多,能够增大碳纤维织物的比表面积。当异形碳纤维制成具有一定厚度的碳纤维织物后,异形碳纤维的排列在一起,异形横截面的空隙相互连通,形成空隙网络结构。石墨烯负载于碳纤维表面及空隙,负载量显著增多,且填充于碳纤维空隙的石墨烯沿碳纤维长度方向上呈二维线状分布,再通过负载于碳纤维表面的石墨烯连通形成三维导电网络结构。接着在石墨烯表面原位生长聚吡咯,形成聚吡咯纳米线构成的三维纳米导电网络结构,最后在其表面负载生物膜,能够防止石墨烯直接与生物膜接触,克服由于石墨烯的抗菌作用,导致生物膜性能降低的问题。(1) In the special-shaped carbon fiber-based biofilm electrode material provided by the present invention, a special-shaped cross-section carbon fiber fabric is selected as the electrode load matrix. , which can increase the specific surface area of the carbon fiber fabric. When the special-shaped carbon fiber is made into a carbon fiber fabric with a certain thickness, the special-shaped carbon fibers are arranged together, and the gaps of the special-shaped cross-section are connected with each other to form a gap network structure. Graphene is loaded on the surface and voids of the carbon fibers, and the load is significantly increased, and the graphene filled in the voids of the carbon fibers is distributed in a two-dimensional line along the length of the carbon fibers, and then connected by the graphene loaded on the surface of the carbon fibers to form a three-dimensional conductive network structure. Then, polypyrrole is grown in situ on the surface of graphene to form a three-dimensional nano-conductive network structure composed of polypyrrole nanowires, and finally a biofilm is loaded on its surface, which can prevent the graphene from directly contacting the biofilm and overcome the antibacterial effect of graphene. Problems leading to reduced biofilm performance.
(2)本发明提供的异形碳纤维基生物膜电极材料的制备方法,通过控制碳纤维厚度及碳纤维之间的间距,能够得到不同石墨烯和聚吡咯负载量的异形横截面碳纤维织物电极基材,从而对电极基材的导电性能进行调控。在负载石墨烯时,浸渍吸附后,再进行抽滤,以提高氧化石墨烯的负载量和负载牢度,减少由于未负载石墨烯和聚吡咯形成的空位,从而提高电极材料的电子传输速率。(2) The preparation method of the special-shaped carbon fiber-based biofilm electrode material provided by the present invention can obtain the special-shaped cross-section carbon fiber fabric electrode substrate with different graphene and polypyrrole loadings by controlling the thickness of the carbon fiber and the spacing between the carbon fibers, thereby The electrical conductivity of the electrode substrate is regulated. When graphene is loaded, after impregnation and adsorption, suction filtration is performed to improve the loading capacity and loading fastness of graphene oxide, and reduce the vacancies formed by unloaded graphene and polypyrrole, thereby improving the electron transfer rate of the electrode material.
(3)本发明提供的异形碳纤维基生物膜电极材料能够用于有机废水的处理,具有电流密度高、处理效率和电降解率高的优点。(3) The special-shaped carbon fiber-based biofilm electrode material provided by the present invention can be used for the treatment of organic wastewater, and has the advantages of high current density, high treatment efficiency and high electrical degradation rate.
附图说明Description of drawings
图1为本发明提供的异形碳纤维基生物膜电极材料的异形碳纤维的横截面示意图;Fig. 1 is the cross-sectional schematic diagram of the special-shaped carbon fiber of the special-shaped carbon fiber-based biofilm electrode material provided by the present invention;
图2为本发明提供的异形碳纤维基生物膜电极材料的异形横截面碳纤维织物的横截面示意图;2 is a schematic cross-sectional view of a special-shaped cross-section carbon fiber fabric of a special-shaped carbon fiber-based biofilm electrode material provided by the present invention;
图3为本发明提供的异形碳纤维基生物膜电极材料的异形横截面碳纤维织物电极基材的横截面示意图。3 is a schematic cross-sectional view of a carbon fiber fabric electrode substrate with a special-shaped cross-section of the special-shaped carbon fiber-based biofilm electrode material provided by the present invention.
具体实施方式detailed description
以下将对本发明各实施例的技术方案进行清楚、完整的描述,显然,所描述的实施例仅仅是本发明的一部分实施例,而不是全部的实施例;基于本发明的实施例,本领域普通技术人员在没有做出创造性劳动的前提下所得到的所有其它实施例,都属于本发明所保护的范围。The technical solutions of the embodiments of the present invention will be clearly and completely described below. Obviously, the described embodiments are only a part of the embodiments of the present invention, rather than all the embodiments; based on the embodiments of the present invention, common All other embodiments obtained by the skilled person without creative work fall within the protection scope of the present invention.
本发明提供的异形碳纤维基生物膜电极材料,包括异形横截面碳纤维织物电极基材以及负载在电极基材上的生物膜,所述异形横截面碳纤维织物电极基材包括异形横截面碳纤维织物及其表面和碳纤维空隙之间负载的石墨烯和聚吡咯,所述聚吡咯负载于所述石墨烯表面形成聚吡咯纳米线,构成三维纳米导电网络结构。选用异形横截面碳纤维织物作为电极负载基体,在异形横截面碳纤维织物中,异形横截面碳纤维不规则排列,使得异形横截面碳纤维之间的空隙较多,能够增大碳纤维织物的比表面积。石墨烯负载于碳纤维表面及空隙,负载量显著增多,且填充于碳纤维空隙的石墨烯沿碳纤维长度方向上呈二维线状分布,再通过负载于碳纤维表面的石墨烯连通形成三维导电网络结构。接着在石墨烯表面原位生长聚吡咯,形成聚吡咯纳米线构成的三维纳米导电网络结构,最后在其表面负载生物膜,能够防止石墨烯直接与生物膜接触,克服由于石墨烯的抗菌作用,导致生物膜性能降低的问题。The special-shaped carbon fiber-based biofilm electrode material provided by the present invention includes a special-shaped cross-section carbon fiber fabric electrode substrate and a biofilm supported on the electrode substrate. The special-shaped cross-section carbon fiber fabric electrode substrate includes a special-shaped cross-section carbon fiber fabric and its Graphene and polypyrrole are loaded between the surface and the carbon fiber voids, and the polypyrrole is loaded on the graphene surface to form polypyrrole nanowires, forming a three-dimensional nano-conductive network structure. The special-shaped cross-section carbon fiber fabric is selected as the electrode load matrix. In the special-shaped cross-section carbon fiber fabric, the irregular cross-section carbon fibers are arranged irregularly, so that there are more gaps between the special-shaped cross-section carbon fibers, which can increase the specific surface area of the carbon fiber fabric. Graphene is loaded on the surface and voids of the carbon fibers, and the load is significantly increased, and the graphene filled in the voids of the carbon fibers is distributed in a two-dimensional line along the length of the carbon fibers, and then connected by the graphene loaded on the surface of the carbon fibers to form a three-dimensional conductive network structure. Then, polypyrrole is grown in situ on the surface of graphene to form a three-dimensional nano-conductive network structure composed of polypyrrole nanowires, and finally a biofilm is loaded on its surface, which can prevent the graphene from directly contacting the biofilm and overcome the antibacterial effect of graphene. Problems leading to reduced biofilm performance.
请参阅图1和图3所示,作为本发明的进一步改进,所述异形横截面为Y形横截面或星形横截面。从图1中可以看出,每一根Y形横截面或星形横截面的碳纤维由于分叉结构,具有较多空隙。从图2和图3可以看出,当碳纤维制成具有一定厚度的碳纤维织物后,碳纤维的排列在一起,异形横截面的空隙相互连通,形成空隙网络结构。当石墨烯和聚吡咯负载填充至空隙处之后,形成三维导电网络结构。Please refer to FIG. 1 and FIG. 3 , as a further improvement of the present invention, the special-shaped cross-section is a Y-shaped cross-section or a star-shaped cross-section. As can be seen from Figure 1, each carbon fiber with a Y-shaped cross-section or a star-shaped cross-section has more voids due to the bifurcated structure. It can be seen from Figures 2 and 3 that when carbon fibers are made into carbon fiber fabrics with a certain thickness, the carbon fibers are arranged together, and the voids of the special-shaped cross-sections are connected to each other to form a void network structure. After the graphene and polypyrrole are loaded into the voids, a three-dimensional conductive network structure is formed.
作为本发明的进一步改进,所述碳纤维织物为聚丙烯腈碳纤维制成的碳布或碳毡。As a further improvement of the present invention, the carbon fiber fabric is carbon cloth or carbon felt made of polyacrylonitrile carbon fiber.
作为本发明的进一步改进,所述碳纤维织物的厚度为0.05mm~1mm,所述聚丙烯腈碳纤维的间距小于100μm。其中,碳纤维的间距是指碳纤维在制成织物时,任意两根相邻碳纤维之间的距离,碳纤维的间距过大,不利于连通导电网络的形成。通过控制碳纤维厚度及碳纤维之间的间距,能够得到不同石墨烯和聚吡咯负载量的异形横截面碳纤维织物电极基材,从而对电极基材的导电性能进行调控。As a further improvement of the present invention, the thickness of the carbon fiber fabric is 0.05 mm˜1 mm, and the spacing of the polyacrylonitrile carbon fibers is less than 100 μm. Among them, the spacing of carbon fibers refers to the distance between any two adjacent carbon fibers when carbon fibers are made into fabrics, and the spacing of carbon fibers is too large, which is not conducive to the formation of a connected conductive network. By controlling the thickness of carbon fibers and the spacing between carbon fibers, special-shaped cross-section carbon fiber fabric electrode substrates with different graphene and polypyrrole loadings can be obtained, so as to control the electrical conductivity of the electrode substrate.
作为本发明的进一步改进,所述生物膜为电活性微生物膜。如好氧菌或厌氧菌微生物膜,根据待处理有机废水中的有机物种类,接种不同的微生物菌落,实现有机废水的微生物电化学降解处理。As a further improvement of the present invention, the biofilm is an electroactive microbial film. Such as aerobic bacteria or anaerobic bacteria microbial membrane, according to the type of organic matter in the organic wastewater to be treated, different microbial colonies are inoculated to realize the microbial electrochemical degradation treatment of organic wastewater.
一种以上所述的异形碳纤维基生物膜电极材料的制备方法,包括以下步骤:A preparation method of the above-mentioned special-shaped carbon fiber-based biofilm electrode material, comprising the following steps:
S1.将异形横截面碳纤维制成厚度为0.05mm~1mm的碳纤维织物。S1. The special-shaped cross-section carbon fiber is made into a carbon fiber fabric with a thickness of 0.05 mm to 1 mm.
S2.将步骤S1所述的碳纤维织物在氧化石墨烯溶液中浸渍吸附1~4h后,进行抽滤,然后还原得到负载石墨烯的碳纤维织物;如采用直接还原剂还原法、微波辅助还原法、紫外辐照还原法、电化学还原法等将氧化石墨烯还原为石墨烯;浸渍吸附后,氧化石墨烯吸附于碳纤维织物表面及碳纤维空隙之间,然后通过抽滤,提高氧化石墨烯的负载量和负载牢度,克服由于未负载 形成的空位导致电极材料的电子传输速率降低的问题。S2. after soaking and adsorbing the carbon fiber fabric described in step S1 in the graphene oxide solution for 1~4h, carry out suction filtration, and then reduce to obtain the carbon fiber fabric loaded with graphene; Graphene oxide is reduced to graphene by ultraviolet irradiation reduction method, electrochemical reduction method, etc.; after impregnation and adsorption, graphene oxide is adsorbed on the surface of carbon fiber fabric and between carbon fiber gaps, and then through suction filtration, the loading capacity of graphene oxide is increased and load fastness, overcoming the problem of reduced electron transport rate of electrode materials due to vacancies formed by unloading.
S3.将步骤S2得到的所述负载石墨烯的碳纤维织物作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在包含吡咯单体和NaClO 4的电解液中,在0.8V的恒定电压下,通过电化学沉积工艺在负载石墨烯的碳纤维织物表面生长聚吡咯纳米线,得到异形横截面碳纤维电极基材; S3. The graphene-loaded carbon fiber fabric obtained in step S2 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is soaked in an electrolyte containing pyrrole monomer and NaClO 4 . In , under a constant voltage of 0.8V, polypyrrole nanowires were grown on the surface of graphene-loaded carbon fiber fabric by electrochemical deposition process to obtain a special-shaped cross-section carbon fiber electrode substrate;
所述吡咯单体的浓度为50~100mg/L,所述NaClO 4的浓度为20~40g/L。通过电化学沉积工艺,有助于形成在石墨烯表面形成聚吡咯纳米线和均匀的导电网络结构,从而提高电极材料的电子传输速率和电流密度。 The concentration of the pyrrole monomer is 50-100 mg/L, and the concentration of the NaClO 4 is 20-40 g/L. Through the electrochemical deposition process, it is helpful to form polypyrrole nanowires and a uniform conductive network structure on the surface of graphene, thereby improving the electron transport rate and current density of the electrode material.
S4.将步骤S3得到的所述异形横截面碳纤维电极基材作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在接种有电活性微生物的电解液中,通直流电进行培养,得到所述异形碳纤维基生物膜电极材料。S4. The special-shaped cross-section carbon fiber electrode substrate obtained in step S3 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is immersed in an electrolyte inoculated with electroactive microorganisms. , culturing with direct current to obtain the special-shaped carbon fiber-based biofilm electrode material.
所述电解液中包含碳源、PBS缓冲液、维生素和微量元素。The electrolyte contains carbon source, PBS buffer, vitamins and trace elements.
进一步的,在步骤S4中,所述碳源为待处理的有机废水中的有机物,如苯酚、含氟有机物、含氮有机物、含磷有机物。所述有机物的浓度为50~120mg/L。生物膜的形成机理为:接种的电活性微生物首先与异形横截面碳纤维电极基材表面黏附,形成微菌落,并融合成生物膜的基底层;与此同时,产生并释放胞外聚合物,随着培养时间的延长,生物膜的结构逐渐复杂化,发育为成熟的生物膜。其表面的生物膜主要是由微生物细胞、胞外聚合物和水体系中无机离子组成,膜内水含量达95%以上,形成一种多孔结构状态。生物膜电极的应用原理是,对自身已具有去除某种污染物能力的微生物进行电刺激,提高其新陈代谢或消耗污染物的速率,并利用电极基体与污染物间的电荷转移作用对污染物实现双重降解。Further, in step S4, the carbon source is organic matter in the organic wastewater to be treated, such as phenol, fluorine-containing organic matter, nitrogen-containing organic matter, and phosphorus-containing organic matter. The concentration of the organic matter is 50-120 mg/L. The formation mechanism of the biofilm is as follows: the inoculated electroactive microorganisms first adhere to the surface of the carbon fiber electrode substrate with special-shaped cross-section to form microcolonies and fuse into the base layer of the biofilm; at the same time, extracellular polymers are produced and released, followed by the formation of microcolonies. With the extension of the culture time, the structure of the biofilm became more complicated and developed into a mature biofilm. The biofilm on the surface is mainly composed of microbial cells, extracellular polymers and inorganic ions in the water system, and the water content in the film is more than 95%, forming a porous structure state. The application principle of biofilm electrodes is to electrically stimulate microorganisms that already have the ability to remove certain pollutants, increase their metabolism or consume pollutants, and use the charge transfer between the electrode substrate and the pollutants. Double degradation.
进一步的,在步骤S4中,所述直流电的电流为3~8mA。Further, in step S4, the current of the direct current is 3-8 mA.
一种以上所述的异形碳纤维基生物膜电极材料,或者以上所述的制备方 法制备的异形碳纤维基生物膜电极材料的应用,所述异形碳纤维基生物膜电极材料用于有机废水的生物膜电解处理。处理方法为,将所述异形碳纤维基生物膜电极材料作为微生物燃料电池的工作电极,将待处理的有机废水配制成电解液,进行电解处理。有机污染物的生物代谢基本过程包括靠近基质、吸附固体基质、分泌胞外酶、吸收可渗透物质和细胞内代谢。微生物首先向某种基质靠近生长,随后吸附在基质表面。当面对大分子的多聚体化合物时,微生物会分泌胞外酶以将部分大分子水解成小分子的可溶性产物,易于被其他微生物降解和矿化。小分子产物通过单纯扩散、促进扩散、主动运输和基团转位4种方式通过细胞膜进入细胞,通过周边代谢途径被降解。Application of the above-mentioned special-shaped carbon fiber-based biofilm electrode material, or the application of the special-shaped carbon fiber-based biofilm electrode material prepared by the above-mentioned preparation method, the special-shaped carbon fiber-based biofilm electrode material is used for biofilm electrolysis of organic wastewater deal with. The treatment method is as follows: using the special-shaped carbon fiber-based biofilm electrode material as the working electrode of the microbial fuel cell, preparing the organic wastewater to be treated into an electrolyte, and performing electrolytic treatment. The basic processes of biological metabolism of organic pollutants include access to substrates, adsorption of solid substrates, secretion of extracellular enzymes, absorption of permeable substances and intracellular metabolism. Microorganisms first grow close to a certain substrate, and then adsorb on the surface of the substrate. When faced with macromolecular multimeric compounds, microorganisms secrete extracellular enzymes to hydrolyze part of macromolecules into soluble products of small molecules, which are easily degraded and mineralized by other microorganisms. Small molecule products enter cells through the cell membrane through four modes: simple diffusion, facilitated diffusion, active transport and group translocation, and are degraded through peripheral metabolic pathways.
实施例1Example 1
一种异形碳纤维基生物膜电极材料,包括Y形横截面PAN碳纤维织物电极基材以及负载在电极基材上的生物膜,所述Y形横截面PAN碳纤维织物电极基材包括Y形横截面PAN碳纤维织物及其表面和碳纤维空隙之间负载的石墨烯和聚吡咯,所述聚吡咯负载于所述石墨烯表面形成聚吡咯纳米线,构成三维纳米导电网络结构。制备方法如下:A special-shaped carbon fiber-based biofilm electrode material, comprising a Y-shaped cross-section PAN carbon fiber fabric electrode substrate and a biofilm supported on the electrode substrate, the Y-shaped cross-section PAN carbon fiber fabric electrode substrate includes a Y-shaped cross-section PAN Graphene and polypyrrole supported between the carbon fiber fabric and its surface and carbon fiber voids, the polypyrrole is supported on the graphene surface to form polypyrrole nanowires, and constitute a three-dimensional nano-conductive network structure. The preparation method is as follows:
S1.将Y形横截面PAN碳纤维制成厚度为0.1mm、碳纤维的间距为80~100μm的碳纤维布;S1. The Y-shaped cross-section PAN carbon fiber is made into a carbon fiber cloth with a thickness of 0.1 mm and a carbon fiber spacing of 80-100 μm;
S2.将步骤S1所述的碳纤维布在氧化石墨烯溶液中浸渍吸附2h后,进行抽滤,浸渍吸附后,氧化石墨烯吸附于碳纤维布表面及碳纤维空隙之间,然后通过抽滤,提高氧化石墨烯的负载量和负载牢度,克服由于未负载形成的空位导致电极材料的电子传输速率降低的问题,然后通过电化学还原法还原得到负载石墨烯的碳纤维布;S2. after the carbon fiber cloth described in step S1 is soaked and adsorbed in the graphene oxide solution for 2h, suction filtration is performed, after the soaking and adsorption, the graphene oxide is adsorbed on the surface of the carbon fiber cloth and between the carbon fiber gaps, and then by suction filtration, to improve oxidation The loading amount and loading fastness of graphene can overcome the problem that the electron transport rate of the electrode material is reduced due to the vacancies formed by unloading, and then the graphene-loaded carbon fiber cloth is obtained by electrochemical reduction method;
S3.将步骤S2得到的所述负载石墨烯的碳纤维布作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在吡咯单体的浓度为65mg/L、NaClO 4的浓度为30g/L的电解液中,在0.8V的恒定电压下,通 过电化学沉积工艺在负载石墨烯的碳纤维织物表面生长聚吡咯纳米线,得到异形横截面碳纤维电极基材;通过电化学沉积工艺,有助于形成在石墨烯表面形成聚吡咯纳米线和均匀的导电网络结构,从而提高电极材料的电子传输速率和电流密度; S3. The graphene-loaded carbon fiber cloth obtained in step S2 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, and the concentration of immersed in the pyrrole monomer is 65mg/L, In an electrolyte with a concentration of NaClO 4 of 30 g/L, under a constant voltage of 0.8 V, polypyrrole nanowires were grown on the surface of the graphene-loaded carbon fiber fabric by an electrochemical deposition process to obtain a special-shaped cross-section carbon fiber electrode substrate; The electrochemical deposition process helps to form polypyrrole nanowires and a uniform conductive network structure on the surface of graphene, thereby improving the electron transfer rate and current density of the electrode material;
S4.将步骤S3得到的所述Y形横截面PAN电极基材作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在接种有苯酚高效降解菌种的电解液中,通5mA的直流电进行培养,得到Y形横截面PAN基生物膜电极材料;所述电解液中包含100mg/L碳源、50mmol/L的PBS缓冲液、10ml/L的维生素和微量元素。S4. The Y-shaped cross-section PAN electrode substrate obtained in step S3 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system. In the electrolyte, the direct current of 5mA is used for cultivation to obtain a Y-shaped cross-section PAN-based biofilm electrode material; the electrolyte contains 100mg/L carbon source, 50mmol/L PBS buffer, 10ml/L vitamins and trace amounts. element.
对比例1Comparative Example 1
一种异形碳纤维基生物膜电极材料,与实施例1相比,不同之处在于,所述PAN碳纤维织物为圆形横截面PAN碳纤维,其他与实施例1大致相同,在此不再赘述。A special-shaped carbon fiber-based biofilm electrode material, compared with Example 1, the difference is that the PAN carbon fiber fabric is a circular cross-section PAN carbon fiber, the other is roughly the same as Example 1, and will not be repeated here.
对比例2Comparative Example 2
一种异形碳纤维基生物膜电极材料,与实施例1相比,不同之处在于,包括Y形横截面PAN碳纤维织物以及负载在碳纤维织物上的生物膜,即未负载石墨烯和聚吡咯,制备方法不包含步骤S2和S3,其他与实施例1大致相同,在此不再赘述。A special-shaped carbon fiber-based biofilm electrode material, compared with Example 1, is different in that it includes a Y-shaped cross-section PAN carbon fiber fabric and a biofilm loaded on the carbon fiber fabric, that is, unloaded graphene and polypyrrole, prepared The method does not include steps S2 and S3, and the others are substantially the same as those in Embodiment 1, which will not be repeated here.
对比例3Comparative Example 3
一种异形碳纤维基生物膜电极材料,与实施例1相比,不同之处在于,所述Y形横截面PAN碳纤维织物电极基材包括Y形横截面PAN碳纤维织物及其表面和碳纤维空隙之间负载的石墨烯,即未负载聚吡咯。其他与实施例1大致相同,在此不再赘述。A special-shaped carbon fiber-based biofilm electrode material, compared with Example 1, the difference is that the Y-shaped cross-section PAN carbon fiber fabric electrode substrate comprises a Y-shaped cross-section PAN carbon fiber fabric and its surface and the carbon fiber voids between Supported graphene, i.e. unsupported polypyrrole. Others are substantially the same as those in Embodiment 1, and are not repeated here.
对比例4Comparative Example 4
一种异形碳纤维基生物膜电极材料,与实施例1相比,不同之处在于, 所述Y形横截面PAN碳纤维织物电极基材包括Y形横截面PAN碳纤维织物及其表面和碳纤维空隙之间负载的聚吡咯,即未负载石墨烯。其他与实施例1大致相同,在此不再赘述。A special-shaped carbon fiber-based biofilm electrode material, compared with Example 1, the difference is that the Y-shaped cross-section PAN carbon fiber fabric electrode substrate comprises a Y-shaped cross-section PAN carbon fiber fabric and the surface between the surface and the carbon fiber voids Supported polypyrrole, i.e. unsupported graphene. Others are substantially the same as those in Embodiment 1, and are not repeated here.
实施例2~4及对比例5Examples 2 to 4 and Comparative Example 5
实施例2~4及对比例5提供的异形碳纤维基生物膜电极材料,与实施例1相比,不同之处在于,所述Y形横截面PAN碳纤维的厚度及碳纤维间隙如表1所示,其他与实施例1大致相同,在此不再赘述。Compared with Example 1, the special-shaped carbon fiber-based biofilm electrode materials provided in Examples 2 to 4 and Comparative Example 5 are different in that the thickness of the Y-shaped cross-section PAN carbon fiber and the carbon fiber gap are shown in Table 1. Others are substantially the same as those in Embodiment 1, and are not repeated here.
表1 实施例2~4及对比例5的制备条件Table 1 Preparation conditions of Examples 2-4 and Comparative Example 5
试样sample Y形横截面PAN碳纤维的厚度(mm)Thickness of Y-shaped cross-section PAN carbon fiber (mm) 碳纤维的间距(μm)Pitch of carbon fibers (μm)
实施例2Example 2 0.050.05 80~10080~100
实施例3Example 3 11 80~10080~100
实施例4Example 4 0.10.1 60~8060~80
对比例5Comparative Example 5 0.10.1 120120
应用例1~4及应用对比例1~5Application examples 1 to 4 and application comparison examples 1 to 5
应用例1~4及应用对比例1~5分别为将实施例1~4及对比例1~5制备的Y形碳纤维基生物膜电极材料用于含苯酚的有机废水的处理,处理方法如下:将所述Y形碳纤维基生物膜电极材料作为微生物燃料电池的工作电极,将含含酚有机废水配制成电解液,进行电解处理,所述有机废水中苯酚浓度为1500mg/L,COD含量为2500mg/L。Application Examples 1 to 4 and Application Comparative Examples 1 to 5 are respectively using the Y-shaped carbon fiber-based biofilm electrode materials prepared in Examples 1 to 4 and Comparative Examples 1 to 5 for the treatment of organic wastewater containing phenol. The treatment methods are as follows: The Y-shaped carbon fiber-based biofilm electrode material is used as the working electrode of the microbial fuel cell, and the organic wastewater containing phenol is prepared into an electrolyte, and electrolytic treatment is performed. The phenol concentration in the organic wastewater is 1500mg/L, and the COD content is 2500mg /L.
表2 应用例1~4及应用对比例1~5的电讲解性能Table 2 Electrical performance of application examples 1 to 4 and application comparison examples 1 to 5
试样sample 电流密度(mA/cm 2) Current density (mA/cm 2 ) 苯酚去除率(%)Phenol removal rate (%) COD转化率(%)COD conversion rate (%)
应用例1Application example 1 278278 99.999.9 95.895.8
应用例2Application example 2 269269 99.899.8 95.695.6
应用例3Application example 3 280280 99.999.9 95.695.6
应用例4Application example 4 271271 99.999.9 95.795.7
应用对比例1Application Example 1 228228 96.396.3 90.290.2
应用对比例2Application Comparative Example 2 109109 89.889.8 81.281.2
应用对比例3Application Comparative Example 3 128128 91.991.9 83.183.1
应用对比例4Application Comparative Example 4 137137 92.892.8 85.085.0
应用对比例5Application Comparative Example 5 232232 97.697.6 90.790.7
从表2可以看出,采用本发明提供的制备方法制备的Y形碳纤维基生物膜电极材料进行生物电降解处理含酚类有机废水,苯酚的去除率高达99%以上,COD转化率高达95%以上。当碳纤维为圆形横截面时,电流密度及苯酚去除率和COD转化率均显著降低,只是因为圆形横截面的碳纤维排列较密集,碳纤维的空隙较少,比表面积降低,导致石墨烯和聚吡咯的负载量降低,且无法通过空隙及表面负载形成三维导电网络结构。当碳纤维为Y形横截面,但未负载石墨烯和聚吡咯时,电流密度及苯酚去除率和COD转化率降低最明显,当只负载石墨烯时,电流密度及苯酚去除率和COD转化率低于只负载聚吡咯的,这是可能因为当石墨烯表面未负载聚吡咯时,石墨烯的抗菌作用会一定程度抑制生物膜的生长,从而降低其性能。当碳纤维的间距大于100μm时,电流密度及苯酚去除率和COD转化率也有所降低,这可能是因为碳纤维的间距过大,不利于连通导电网络的形成,未负载石墨烯和聚吡咯形成的空位增多,导致电极材料的电子传输速率降低。As can be seen from Table 2, the Y-shaped carbon fiber-based biofilm electrode material prepared by the preparation method provided by the present invention is used for bioelectric degradation treatment of phenolic organic wastewater, the removal rate of phenol is as high as 99%, and the conversion rate of COD is as high as 95% above. When the carbon fiber has a circular cross-section, the current density, phenol removal rate and COD conversion rate are significantly reduced, just because the carbon fiber with a circular cross-section is densely arranged, the carbon fiber has fewer voids, and the specific surface area is reduced, resulting in graphene and polymer The loading of pyrrole is reduced, and the three-dimensional conductive network structure cannot be formed through voids and surface loading. When the carbon fiber has a Y-shaped cross section, but no graphene and polypyrrole are supported, the current density, phenol removal rate and COD conversion rate decrease most obviously. When only graphene is supported, the current density, phenol removal rate and COD conversion rate are low. This is probably because when the graphene surface is not loaded with polypyrrole, the antibacterial effect of graphene will inhibit the growth of biofilms to a certain extent, thereby reducing its performance. When the spacing of carbon fibers is greater than 100 μm, the current density, phenol removal rate and COD conversion rate also decrease. This may be because the spacing of carbon fibers is too large, which is not conducive to the formation of a connected conductive network, and the vacancies formed by graphene and polypyrrole are not supported. increase, resulting in a decrease in the electron transport rate of the electrode material.
以上所述,仅为本发明较佳的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,根据本发明的技术方案及其发明构思加以等同替换或改变,都应涵盖在本发明的保护范围之内。The above description is only a preferred embodiment of the present invention, but the protection scope of the present invention is not limited to this. The equivalent replacement or change of the inventive concept thereof shall be included within the protection scope of the present invention.

Claims (10)

  1. 一种异形碳纤维基生物膜电极材料,其特征在于,包括异形横截面碳纤维织物电极基材以及负载在电极基材上的生物膜,所述异形横截面碳纤维织物电极基材包括异形横截面碳纤维织物及其表面和碳纤维空隙之间负载的石墨烯和聚吡咯,所述聚吡咯负载于所述石墨烯表面形成聚吡咯纳米线,构成三维纳米导电网络结构。A special-shaped carbon fiber-based biofilm electrode material, characterized in that it includes a carbon fiber fabric electrode substrate with a special-shaped cross-section and a biofilm supported on the electrode substrate, and the carbon fiber fabric electrode substrate with a special-shaped cross-section comprises a carbon fiber fabric with a special-shaped cross-section Graphene and polypyrrole supported between its surface and carbon fiber voids, and the polypyrrole is supported on the graphene surface to form polypyrrole nanowires, forming a three-dimensional nano-conductive network structure.
  2. 根据权利要求1所述的异形碳纤维基生物膜电极材料,其特征在于,所述异形横截面为Y形横截面或星形横截面。The special-shaped carbon fiber-based biofilm electrode material according to claim 1, wherein the special-shaped cross-section is a Y-shaped cross-section or a star-shaped cross-section.
  3. 根据权利要求2所述的异形碳纤维基生物膜电极材料,其特征在于,所述碳纤维织物为聚丙烯腈碳纤维制成的碳布或碳毡。The special-shaped carbon fiber-based biofilm electrode material according to claim 2, wherein the carbon fiber fabric is carbon cloth or carbon felt made of polyacrylonitrile carbon fiber.
  4. 根据权利要求3所述的异形碳纤维基生物膜电极材料,其特征在于,所述碳纤维织物的厚度为0.05mm~1mm,所述聚丙烯腈碳纤维的间距小于100μm。The special-shaped carbon fiber-based biofilm electrode material according to claim 3, wherein the thickness of the carbon fiber fabric is 0.05 mm to 1 mm, and the spacing between the polyacrylonitrile carbon fibers is less than 100 μm.
  5. 根据权利要求1所述的异形碳纤维基生物膜电极材料,其特征在于,所述生物膜为电活性微生物膜。The special-shaped carbon fiber-based biofilm electrode material according to claim 1, wherein the biofilm is an electroactive microbial film.
  6. 一种权利要求1至5中任一项所述的异形碳纤维基生物膜电极材料的制备方法,其特征在于,包括以下步骤:A method for preparing a special-shaped carbon fiber-based biofilm electrode material according to any one of claims 1 to 5, characterized in that, comprising the following steps:
    S1.将异形横截面碳纤维制成厚度为0.05mm~1mm的碳纤维织物;S1. The special-shaped cross-section carbon fiber is made into a carbon fiber fabric with a thickness of 0.05mm to 1mm;
    S2.将步骤S1所述碳纤维织物在氧化石墨烯溶液中浸渍吸附后,进行抽滤,然后还原得到负载石墨烯的碳纤维织物;S2. after the carbon fiber fabric described in step S1 is impregnated and adsorbed in the graphene oxide solution, suction filtration is performed, and then the carbon fiber fabric loaded with graphene is obtained by reduction;
    S3.将步骤S2得到的所述负载石墨烯的碳纤维织物作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在包含吡咯单体和NaClO 4的电解液中,通过电化学沉积工艺在负载石墨烯的碳纤维织物表面生长聚吡咯纳米线,得到异形横截面碳纤维电极基材; S3. The graphene-loaded carbon fiber fabric obtained in step S2 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is soaked in an electrolyte containing pyrrole monomer and NaClO 4 . In , polypyrrole nanowires are grown on the surface of graphene-loaded carbon fiber fabric by electrochemical deposition process to obtain a special-shaped cross-section carbon fiber electrode substrate;
    S4.将步骤S3得到的所述异形横截面碳纤维电极基材作为工作电极,铂电极作为对电极,Ag/AgCl作为参比电极,构建三电极体系,浸泡在接种有电 活性微生物的电解液中,通直流电进行培养,得到所述异形碳纤维基生物膜电极材料;S4. The special-shaped cross-section carbon fiber electrode substrate obtained in step S3 is used as the working electrode, the platinum electrode is used as the counter electrode, and the Ag/AgCl is used as the reference electrode to construct a three-electrode system, which is immersed in an electrolyte inoculated with electroactive microorganisms. , culturing with direct current to obtain the special-shaped carbon fiber-based biofilm electrode material;
    所述电解液中包含碳源、PBS缓冲液、维生素和微量元素。The electrolyte contains carbon source, PBS buffer, vitamins and trace elements.
  7. 根据权利要求6所述的异形碳纤维基生物膜电极材料的制备方法,其特征在于,在步骤S3中,所述吡咯单体的浓度为50~100mg/L,所述NaClO 4的浓度为20~40g/L。 The method for preparing a special-shaped carbon fiber-based biofilm electrode material according to claim 6, wherein in step S3, the concentration of the pyrrole monomer is 50-100 mg/L, and the concentration of the NaClO 4 is 20-100 mg/L. 40g/L.
  8. 根据权利要求6所述的异形碳纤维基生物膜电极材料的制备方法,其特征在于,在步骤S4中,所述碳源为待处理的有机废水中的有机物,所述有机物的浓度为50~120mg/L。The method for preparing a special-shaped carbon fiber-based biofilm electrode material according to claim 6, wherein in step S4, the carbon source is organic matter in the organic wastewater to be treated, and the concentration of the organic matter is 50-120 mg /L.
  9. 根据权利要求6所述的异形碳纤维基生物膜电极材料的制备方法,其特征在于,在步骤S4中,所述直流电的电流为3~8mA。The method for preparing a special-shaped carbon fiber-based biofilm electrode material according to claim 6, wherein in step S4, the current of the direct current is 3-8 mA.
  10. 一种权利要求1至5中任一项所述的异形碳纤维基生物膜电极材料,或者权利要求6至9中任一项所述的制备方法制备的异形碳纤维基生物膜电极材料的应用,其特征在于,所述异形碳纤维基生物膜电极材料用于有机废水的生物膜电解处理。A special-shaped carbon fiber-based biofilm electrode material according to any one of claims 1 to 5, or the application of the special-shaped carbon fiber-based biofilm electrode material prepared by the preparation method according to any one of claims 6 to 9, which It is characterized in that the special-shaped carbon fiber-based biofilm electrode material is used for biofilm electrolysis treatment of organic wastewater.
PCT/CN2020/099699 2020-07-01 2020-07-01 Biomembrane electrode material based on special-shaped carbon fiber, and preparation method therefor and use thereof WO2022000364A1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
PCT/CN2020/099699 WO2022000364A1 (en) 2020-07-01 2020-07-01 Biomembrane electrode material based on special-shaped carbon fiber, and preparation method therefor and use thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
PCT/CN2020/099699 WO2022000364A1 (en) 2020-07-01 2020-07-01 Biomembrane electrode material based on special-shaped carbon fiber, and preparation method therefor and use thereof

Publications (1)

Publication Number Publication Date
WO2022000364A1 true WO2022000364A1 (en) 2022-01-06

Family

ID=79317786

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/CN2020/099699 WO2022000364A1 (en) 2020-07-01 2020-07-01 Biomembrane electrode material based on special-shaped carbon fiber, and preparation method therefor and use thereof

Country Status (1)

Country Link
WO (1) WO2022000364A1 (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20040170886A1 (en) * 2002-12-02 2004-09-02 Sanyo Electric Co., Ltd. Fuel cell and material of gas diffusion layer
CN106283610A (en) * 2016-08-04 2017-01-04 武汉纺织大学 A kind of Graphene inductive formation polypyrrole nano line conducing composite material preparation method
US20170141424A1 (en) * 2015-11-11 2017-05-18 Bioenergysp, Inc. Method and apparatus for converting chemical energy stored in wastewater
CN107799796A (en) * 2017-09-19 2018-03-13 华南师范大学 A kind of anode of microbial fuel cell of nitrogen modification and preparation method thereof
CN109537106A (en) * 2018-11-09 2019-03-29 中国科学院山西煤炭化学研究所 The method that high-speed dry spray spinning prepares Irregular Section Carbon Fiber precursor fibre, pre-oxidized fibers or carbon fiber
CN110447139A (en) * 2018-03-02 2019-11-12 住友电气工业株式会社 Redox flow batteries electrode, redox flow batteries unit and redox flow batteries

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20040170886A1 (en) * 2002-12-02 2004-09-02 Sanyo Electric Co., Ltd. Fuel cell and material of gas diffusion layer
US20170141424A1 (en) * 2015-11-11 2017-05-18 Bioenergysp, Inc. Method and apparatus for converting chemical energy stored in wastewater
CN106283610A (en) * 2016-08-04 2017-01-04 武汉纺织大学 A kind of Graphene inductive formation polypyrrole nano line conducing composite material preparation method
CN107799796A (en) * 2017-09-19 2018-03-13 华南师范大学 A kind of anode of microbial fuel cell of nitrogen modification and preparation method thereof
CN110447139A (en) * 2018-03-02 2019-11-12 住友电气工业株式会社 Redox flow batteries electrode, redox flow batteries unit and redox flow batteries
CN109537106A (en) * 2018-11-09 2019-03-29 中国科学院山西煤炭化学研究所 The method that high-speed dry spray spinning prepares Irregular Section Carbon Fiber precursor fibre, pre-oxidized fibers or carbon fiber

Similar Documents

Publication Publication Date Title
Ghasemi et al. The effect of nitric acid, ethylenediamine, and diethanolamine modified polyaniline nanoparticles anode electrode in a microbial fuel cell
Yuan et al. Nanostructured macroporous bioanode based on polyaniline-modified natural loofah sponge for high-performance microbial fuel cells
Choi et al. Enhanced power production of a membrane electrode assembly microbial fuel cell (MFC) using a cost effective poly [2, 5-benzimidazole](ABPBI) impregnated non-woven fabric filter
Jiang et al. Granular activated carbon single-chamber microbial fuel cells (GAC-SCMFCs): a design suitable for large-scale wastewater treatment processes
Zhang et al. Performance improvement of air-cathode single-chamber microbial fuel cell using a mesoporous carbon modified anode
CN109216717B (en) Catalyst, method for preparing the same, cathode and electrochemical system
Li et al. Performance of carbon fiber cathode membrane with C–Mn–Fe–O catalyst in MBR–MFC for wastewater treatment
KR100446406B1 (en) A Membraneless And Mediatorless Microbial Fuel Cell
Karthikeyan et al. Effect of composites based nickel foam anode in microbial fuel cell using Acetobacter aceti and Gluconobacter roseus as a biocatalysts
Song et al. Effect of different acclimation methods on the performance of microbial fuel cells using phenol as substrate
JP2004342412A (en) Power generation method and device using organic substance
Yuan et al. Wiring microbial biofilms to the electrode by osmium redox polymer for the performance enhancement of microbial fuel cells
Liu et al. Influence of soluble microbial products on the long-term stability of air cathodes in microbial fuel cells
CN104701561B (en) Photoelectric-microbiological composite anode microbial fuel cell and method for processing domestic sewage by using microbial fuel cell
Huang et al. Long-term electricity generation and denitrification performance of MFCs with different exchange membranes and electrode materials
Li et al. Response of anodic biofilm and the performance of microbial fuel cells to different discharging current densities
Zhang et al. Long-term effect of carbon nanotubes on electrochemical properties and microbial community of electrochemically active biofilms in microbial fuel cells
WO2011025021A1 (en) Electrode for microbial fuel cell, and microbial fuel cell using same
CN109052578B (en) Method for treating wastewater by using modified electrode in continuous flow bioelectricity Fenton system
Jiang et al. Iron cobalt-doped carbon nanofibers anode to simultaneously boost bioelectrocatalysis and direct electron transfer in microbial fuel cells: Characterization, performance, and mechanism
CN103265149A (en) Power supply-free electric adsorption wastewater treatment device and method
Xu et al. Cathode modification with peptide nanotubes (PNTs) incorporating redox mediators for azo dyes decolorization enhancement in microbial fuel cells
Fei et al. Electrophoretic deposition of carbon nanotube on reticulated vitreous carbon for hexavalent chromium removal in a biocathode microbial fuel cell
Li et al. Microbial fuel cells in power generation and extended applications
HASSAN et al. AJ Csian OURNALOF HEMISTRY AJ Csian OURNALOF HEMISTRY

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 20942594

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: DE

32PN Ep: public notification in the ep bulletin as address of the adressee cannot be established

Free format text: NOTING OF LOSS OF RIGHTS PURSUANT TO RULE 112(1) EPC (EPO FORM 1205A DATED 06.06.2023)

122 Ep: pct application non-entry in european phase

Ref document number: 20942594

Country of ref document: EP

Kind code of ref document: A1