CN107180988B - Microbial fuel cell and sewage treatment device - Google Patents
Microbial fuel cell and sewage treatment device Download PDFInfo
- Publication number
- CN107180988B CN107180988B CN201710500473.1A CN201710500473A CN107180988B CN 107180988 B CN107180988 B CN 107180988B CN 201710500473 A CN201710500473 A CN 201710500473A CN 107180988 B CN107180988 B CN 107180988B
- Authority
- CN
- China
- Prior art keywords
- sewage treatment
- microbial fuel
- fuel cell
- cathode
- anode
- Prior art date
- Legal status (The legal status 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 status listed.)
- Active
Links
- 239000010865 sewage Substances 0.000 title claims abstract description 178
- 230000000813 microbial effect Effects 0.000 title claims abstract description 115
- 239000000446 fuel Substances 0.000 title claims abstract description 113
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 40
- 238000000926 separation method Methods 0.000 claims abstract description 19
- 239000010406 cathode material Substances 0.000 claims abstract description 17
- 239000012528 membrane Substances 0.000 claims abstract description 17
- 244000005700 microbiome Species 0.000 claims abstract description 14
- 239000010405 anode material Substances 0.000 claims abstract description 9
- 238000011084 recovery Methods 0.000 claims description 17
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 16
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims description 13
- 238000005273 aeration Methods 0.000 claims description 12
- 239000004744 fabric Substances 0.000 claims description 12
- 239000002245 particle Substances 0.000 claims description 10
- 229910002804 graphite Inorganic materials 0.000 claims description 6
- 239000010439 graphite Substances 0.000 claims description 6
- 229910001220 stainless steel Inorganic materials 0.000 claims description 6
- 239000010935 stainless steel Substances 0.000 claims description 6
- 229920000049 Carbon (fiber) Polymers 0.000 claims description 4
- 239000004677 Nylon Substances 0.000 claims description 4
- 239000004917 carbon fiber Substances 0.000 claims description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims description 4
- 229920001778 nylon Polymers 0.000 claims description 4
- 239000004033 plastic Substances 0.000 claims description 4
- 229920003023 plastic Polymers 0.000 claims description 4
- 239000003011 anion exchange membrane Substances 0.000 claims description 3
- 238000005341 cation exchange Methods 0.000 claims description 3
- 239000003365 glass fiber Substances 0.000 claims description 3
- 239000002351 wastewater Substances 0.000 abstract description 21
- 238000000034 method Methods 0.000 abstract description 20
- 230000005611 electricity Effects 0.000 abstract description 16
- 230000008569 process Effects 0.000 abstract description 12
- 230000009286 beneficial effect Effects 0.000 abstract description 7
- 238000001914 filtration Methods 0.000 abstract description 5
- 238000004519 manufacturing process Methods 0.000 abstract description 5
- 238000010276 construction Methods 0.000 abstract description 3
- 230000003321 amplification Effects 0.000 abstract description 2
- 238000003199 nucleic acid amplification method Methods 0.000 abstract description 2
- 239000002994 raw material Substances 0.000 abstract description 2
- 239000000463 material Substances 0.000 description 18
- 230000000694 effects Effects 0.000 description 12
- 238000010248 power generation Methods 0.000 description 11
- 239000000126 substance Substances 0.000 description 10
- 238000000746 purification Methods 0.000 description 8
- 230000008901 benefit Effects 0.000 description 6
- 239000003034 coal gas Substances 0.000 description 6
- 238000013461 design Methods 0.000 description 6
- 238000009826 distribution Methods 0.000 description 6
- 238000005265 energy consumption Methods 0.000 description 6
- 238000004065 wastewater treatment Methods 0.000 description 6
- 238000010586 diagram Methods 0.000 description 5
- 239000010842 industrial wastewater Substances 0.000 description 5
- 239000005416 organic matter Substances 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 4
- 230000009467 reduction Effects 0.000 description 4
- 229910052719 titanium Inorganic materials 0.000 description 4
- 239000010936 titanium Substances 0.000 description 4
- 238000011160 research Methods 0.000 description 3
- 230000001360 synchronised effect Effects 0.000 description 3
- 239000003990 capacitor Substances 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000004146 energy storage Methods 0.000 description 2
- 239000004800 polyvinyl chloride Substances 0.000 description 2
- 238000010923 batch production Methods 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 238000006757 chemical reactions by type Methods 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 230000010354 integration Effects 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 229920000915 polyvinyl chloride Polymers 0.000 description 1
- 238000011946 reduction process Methods 0.000 description 1
- 238000013341 scale-up Methods 0.000 description 1
- 230000035939 shock Effects 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
Classifications
-
- H—ELECTRICITY
- H01—ELECTRIC ELEMENTS
- H01M—PROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
- H01M8/00—Fuel cells; Manufacture thereof
- H01M8/16—Biochemical fuel cells, i.e. cells in which microorganisms function as catalysts
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/005—Combined electrochemical biological processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/301—Aerobic and anaerobic treatment in the same reactor
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/50—Fuel cells
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P70/00—Climate change mitigation technologies in the production process for final industrial or consumer products
- Y02P70/50—Manufacturing or production processes characterised by the final manufactured product
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Engineering & Computer Science (AREA)
- Biodiversity & Conservation Biology (AREA)
- Organic Chemistry (AREA)
- Water Supply & Treatment (AREA)
- Environmental & Geological Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Electrochemistry (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Sustainable Energy (AREA)
- Sustainable Development (AREA)
- Manufacturing & Machinery (AREA)
- Biochemistry (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
Abstract
Description
技术领域technical field
本发明涉及污水处理技术领域,具体的,本发明涉及微生物燃料电池、污水处理装置。The invention relates to the technical field of sewage treatment, in particular, the invention relates to a microbial fuel cell and a sewage treatment device.
背景技术Background technique
目前,环境问题与能源问题是社会发展面临的两大难题。微生物燃料电池不仅能够实现电能的输出,还可以在产生电能的同时,利用产电微生物将污水中的有机物分解,从而实现污水的处理。具体的,利用附着在阳极的产电微生物将污水中的有机物氧化,同时阴极接受电子完成还原半反应。阴极电势高于阳极电势时即可对外输出电能。At present, environmental issues and energy issues are two major problems facing social development. Microbial fuel cells can not only realize the output of electric energy, but also use electricity-producing microorganisms to decompose organic matter in sewage while generating electric energy, thereby realizing sewage treatment. Specifically, the electrogenic microorganisms attached to the anode are used to oxidize the organic matter in the sewage, while the cathode accepts electrons to complete the reduction half-reaction. When the potential of the cathode is higher than the potential of the anode, electric energy can be output externally.
然而,目前的微生物燃料电池、污水处理装置仍有待改进。However, the current microbial fuel cells and sewage treatment devices still need to be improved.
发明内容Contents of the invention
本发明旨在至少在一定程度上解决相关技术中的技术问题之一。The present invention aims to solve one of the technical problems in the related art at least to a certain extent.
本发明的发明人在研究过程中,提供了一种微生物燃料电池以及污水处理装置。During the research process, the inventor of the present invention provided a microbial fuel cell and a sewage treatment device.
该微生物燃料电池在工作时,污水经位于外侧的阳极层、分隔膜和阴极层,最终由中空的支撑骨架流出。该微生物燃料电池在工作过程中,可将微生物分解污水中COD的过程与水过滤过程进行结合起来,阳极层负载有的产电微生物还可将污水中有机物氧化,产生电子并被阴极层接收,从而完成还原半反应。如此,在净化污水的同时,该微生物燃料电池还可有效地产电,并且能处理高浓度有机废水。而且该微生物燃料电池的耐冲击负荷能力高;还可作为污水处理装置的核心模块,组装到污水处理装置中,从而具有模块化的特征,易于应用到不同规模的污水处理装置,利于反应器的放大与规模化。When the microbial fuel cell is working, the sewage passes through the outer anode layer, separation membrane and cathode layer, and finally flows out from the hollow support frame. During the working process of the microbial fuel cell, the microbial decomposition of COD in the sewage can be combined with the water filtration process. The electricity-producing microorganisms loaded on the anode layer can also oxidize the organic matter in the sewage to generate electrons and be received by the cathode layer. Thus completing the reduction half reaction. In this way, while purifying sewage, the microbial fuel cell can also effectively generate electricity and can treat high-concentration organic wastewater. Moreover, the microbial fuel cell has a high impact load resistance; it can also be used as a core module of a sewage treatment device and assembled into a sewage treatment device, so it has a modular feature and is easy to apply to sewage treatment devices of different scales, which is beneficial to the reactor. Amplify and scale.
该污水处理装置包括了进水单元、微生物燃料电池、出水单元和电能回收单元,构造紧凑简约,易于实现装置构型的放大;作为一种模块化、组件式的污水处理与能量回收利用装置,具有低能耗、耐冲击负荷、可利用污水化学能产生电能等特点,不仅可以用于生活污水的处理,更可以应用于高浓度有机工业废水的处理,具体例如煤制气废水的处理。The sewage treatment device includes a water inlet unit, a microbial fuel cell, a water outlet unit, and an electric energy recovery unit. The structure is compact and simple, and it is easy to realize the enlargement of the device configuration; It has the characteristics of low energy consumption, impact load resistance, and the use of sewage chemical energy to generate electricity. It can not only be used for domestic sewage treatment, but also can be applied to the treatment of high-concentration organic industrial wastewater, such as the treatment of coal gas wastewater.
有鉴于此,本发明的一个目的在于提出一种既可处理低浓度的生活污水、也可处理高浓度有机废水、可利用污水化学能产生电能或者制造成本低的微生物燃料电池。In view of this, an object of the present invention is to propose a microbial fuel cell that can treat both low-concentration domestic sewage and high-concentration organic wastewater, can use sewage chemical energy to generate electricity, or has low manufacturing cost.
在本发明的第一方面,本发明提出了一种微生物燃料电池。In a first aspect of the invention, the invention proposes a microbial fuel cell.
根据本发明的实施例,所述微生物燃料电池包括:支撑骨架,所述支撑骨架具有与外界连通的腔室;阴极层,所述阴极层设置在所述支撑骨架远离所述腔室的一侧,并环绕所述支撑骨架,且所述阴极层由阴极材料形成;分隔膜,所述分隔膜环绕所述阴极层设置;以及阳极层,所述阳极层环绕所述分隔膜设置,且所述阳极层由阳极材料形成且负载有微生物。According to an embodiment of the present invention, the microbial fuel cell includes: a supporting framework, the supporting framework has a chamber communicating with the outside world; a cathode layer, the cathode layer is arranged on the side of the supporting framework away from the chamber , and surround the support frame, and the cathode layer is formed of a cathode material; a separation film, the separation film is disposed around the cathode layer; and an anode layer, the anode layer is disposed around the separation film, and the The anode layer is formed of an anode material and is loaded with microorganisms.
发明人意外地发现,本发明实施例的微生物燃料电池能够将微生物分解有机污染物的过程以及水过滤过程进行有机结合,阳极负载有的产电微生物将污水中有机物氧化,产生电子并被阴极接收从而完成还原半反应。如此,在净化污水的同时,该微生物燃料电池还可有效地产电,并且能处理高浓度有机废水;而且其耐冲击负荷能力高,可组装到污水处理装置中,还具有模块化的特征,利于污水处理装置的放大与规模化;易于搭建,制造原料成本低,有利于工业化推广的潜力。The inventor unexpectedly found that the microbial fuel cell of the embodiment of the present invention can organically combine the process of microorganisms decomposing organic pollutants and the process of water filtration, and the electricity-producing microorganisms loaded on the anode oxidize the organic matter in the sewage, generate electrons and receive them by the cathode Thus completing the reduction half reaction. In this way, while purifying sewage, the microbial fuel cell can also effectively generate electricity, and can treat high-concentration organic wastewater; and it has a high impact load resistance, can be assembled into a sewage treatment device, and has modular features, which is beneficial to Amplification and scale of sewage treatment equipment; easy to build, low cost of manufacturing raw materials, and conducive to the potential of industrialization.
另外,根据本发明上述实施例的微生物燃料电池,还可以具有如下附加的技术特征:In addition, the microbial fuel cell according to the above-mentioned embodiments of the present invention may also have the following additional technical features:
根据本发明的实施例,所述分隔膜选自玻璃纤维、滤布、塑料网、尼龙布、阳离子交换膜和阴离子交换膜的至少之一。According to an embodiment of the present invention, the separation membrane is selected from at least one of glass fiber, filter cloth, plastic mesh, nylon cloth, cation exchange membrane and anion exchange membrane.
根据本发明的实施例,所述阴极材料以及所述阳极材料分别独立地选自活性炭颗粒、石墨颗粒和碳纤维布的至少之一。According to an embodiment of the present invention, the cathode material and the anode material are independently selected from at least one of activated carbon particles, graphite particles and carbon fiber cloth.
根据本发明的实施例,所述阴极层进一步包括第一阴极集电网以及第二阴极集电网,且所述第一阴极集电网以及所述第二阴极集电网分别设置在所述阴极材料的两侧。According to an embodiment of the present invention, the cathode layer further includes a first cathode collector network and a second cathode collector network, and the first cathode collector network and the second cathode collector network are respectively arranged on two sides of the cathode material. side.
根据本发明的实施例,所述阳极层进一步包括第一阳极集电网以及第二阳极集电网,且所述第一阳极集电网以及所述第二阳极集电网分别设置在所述阴极材料的两侧。According to an embodiment of the present invention, the anode layer further includes a first anode collector grid and a second anode collector grid, and the first anode collector grid and the second anode collector grid are respectively arranged on both sides of the cathode material. side.
根据本发明的实施例,所述第一阴极集电网、所述第二阴极集电网、所述第一阳极集电网和所述第二阳极集电网,各自独立地为钛网或不锈钢网。According to an embodiment of the present invention, the first cathode grid, the second cathode grid, the first anode grid and the second anode grid are each independently titanium mesh or stainless steel mesh.
根据本发明的实施例,所述微生物燃料电池进一步包括:支撑层,所述支撑层设置在所述阳极层的外壁,且所述支撑层为钛网或不锈钢网。According to an embodiment of the present invention, the microbial fuel cell further includes: a support layer, the support layer is arranged on the outer wall of the anode layer, and the support layer is a titanium mesh or a stainless steel mesh.
在本发明的第二方面,本发明提出了一种污水处理装置。In a second aspect of the present invention, the present invention provides a sewage treatment device.
根据本发明的实施例,所述污水处理装置包括:污水处理单元,所述污水处理单元包括至少一个上述的微生物燃料电池;进水单元,所述进水单元用于向所述污水处理单元供给污水;出水单元,所述出水单元与所述污水处理单元相连,用于收集所述微生物燃料电池过滤后的水;以及电能回收单元,所述电能回收单元与污水处理单元电连接。According to an embodiment of the present invention, the sewage treatment device includes: a sewage treatment unit, the sewage treatment unit includes at least one of the above-mentioned microbial fuel cells; a water inlet unit, the water inlet unit is used to supply the sewage treatment unit with Sewage; a water outlet unit connected to the sewage treatment unit for collecting water filtered by the microbial fuel cell; and an electric energy recovery unit electrically connected to the sewage treatment unit.
发明人意外地发现,本发明实施例的污水处理装置,其构造紧凑简约、易于实现装置构型的放大;作为一种模块化、组件式的污水处理与能量回收利用装置,具有低能耗、耐冲击负荷、可利用污水化学能产生电能等特点,既可以用于生活污水的处理,也可用于工业废水的处理。本领域技术人员能够理解的是,前面针对微生物燃料电池所描述的特征和优点,仍适用于该污水处理装置,在此不再赘述。The inventor unexpectedly found that the sewage treatment device of the embodiment of the present invention has a compact and simple structure and is easy to realize the enlargement of the device configuration; as a modularized and componentized sewage treatment and energy recovery device, it has low energy consumption, durable Shock load, the use of sewage chemical energy to generate electricity and other characteristics, can be used not only for domestic sewage treatment, but also for industrial wastewater treatment. Those skilled in the art can understand that the features and advantages described above for the microbial fuel cell are still applicable to the sewage treatment device, and will not be repeated here.
另外,根据本发明上述实施例的污水处理装置,还可以具有如下附加的技术特征:In addition, the sewage treatment device according to the above-mentioned embodiments of the present invention may also have the following additional technical features:
根据本发明的实施例,所述污水处理装置进一步包括:曝气单元,所述曝气单元的至少一部分设置在所述微生物燃料电池的阴极层内。According to an embodiment of the present invention, the sewage treatment device further includes: an aeration unit, at least a part of the aeration unit is disposed in the cathode layer of the microbial fuel cell.
根据本发明的实施例,所述曝气单元包括穿孔管。According to an embodiment of the present invention, the aeration unit comprises a perforated pipe.
根据本发明的实施例,所述污水处理装置包括多个所述污水处理单元,且所述多个污水处理单元之间并联设置。According to an embodiment of the present invention, the sewage treatment device includes a plurality of sewage treatment units, and the plurality of sewage treatment units are arranged in parallel.
根据本发明的实施例,所述污水处理装置包括多个所述污水处理单元,且所述多个污水处理单元之间串联设置。According to an embodiment of the present invention, the sewage treatment device includes a plurality of sewage treatment units, and the plurality of sewage treatment units are arranged in series.
本发明的附加方面和优点将在下面的描述中部分给出,部分将从下面的描述中变得明显,或通过本发明的实践了解到。Additional aspects and advantages of the invention will be set forth in the description which follows, and in part will be obvious from the description, or may be learned by practice of the invention.
附图说明Description of drawings
本发明的上述和/或附加的方面和优点从结合下面附图对实施例的描述中将变得明显和容易理解,其中:The above and/or additional aspects and advantages of the present invention will become apparent and understandable from the description of the embodiments in conjunction with the following drawings, wherein:
图1是本发明一个实施例的微生物燃料电池的横截面的结构示意图;Fig. 1 is the structural representation of the cross section of the microbial fuel cell of an embodiment of the present invention;
图2是本发明一个实施例的微生物燃料电池的纵截面的结构示意图;Fig. 2 is the structural representation of the longitudinal section of the microbial fuel cell of an embodiment of the present invention;
图3是本发明另一个实施例的微生物燃料电池的横截面的结构示意图;Fig. 3 is the structural representation of the cross section of the microbial fuel cell of another embodiment of the present invention;
图4是本发明一个实施例的污水处理装置的结构示意图;Fig. 4 is a schematic structural view of a sewage treatment device according to an embodiment of the present invention;
图5是本发明另一个实施例的污水处理装置的主视结构示意图;Fig. 5 is a front structural schematic diagram of a sewage treatment device according to another embodiment of the present invention;
图6是本发明另一个实施例的污水处理装置的俯视结构示意图;6 is a schematic top view of a sewage treatment device according to another embodiment of the present invention;
图7是本发明另一个实施例的污水处理装置的配水槽堰板的立面结构示意图;Fig. 7 is a schematic diagram of the facade structure of the weir plate of the water distribution tank of the sewage treatment device according to another embodiment of the present invention;
图8是本发明一个实施例的污水处理装置的处理煤制气废水COD变化图;Fig. 8 is a COD change diagram of coal-gas wastewater treated by a sewage treatment device according to an embodiment of the present invention;
图9是本发明一个实施例的污水处理装置的处理煤制气废水同步产电图;Fig. 9 is a diagram of synchronous power generation of coal-gas wastewater treated by a sewage treatment device according to an embodiment of the present invention;
图10是本发明一个实施例的污水处理装置的处理煤制气废水同步产电功率图。Fig. 10 is a power diagram of synchronous power generation for coal-to-gas wastewater treatment by a sewage treatment device according to an embodiment of the present invention.
附图标记reference sign
10 支撑骨架10 Support skeleton
20 阴极层20 cathode layer
21 第一阴极集电网21 The first cathode grid
22 第二阴极集电网22 Second cathode grid
30 分隔膜30 separator film
40 阳极层40 anode layer
41 第一阳极集电网41 The first anode collector grid
42 第二阳极集电网42 Second anode collector grid
50 支撑层50 support layers
100 微生物燃料电池100 microbial fuel cells
200 污水处理单元200 sewage treatment unit
300 进水单元300 water inlet unit
310 配水槽310 distribution tank
3110 配水槽堰板3110 Distribution tank weir plate
400 出水单元400 outlet unit
500 电能回收单元500 Power Recovery Unit
600 曝气单元600 aeration unit
具体实施方式Detailed ways
下面详细描述本发明的实施例,本技术领域人员会理解,下面实施例旨在用于解释本发明,而不应视为对本发明的限制。除非特别说明,在下面实施例中没有明确描述具体技术或条件的,本领域技术人员可以按照本领域内的常用的技术或条件或按照产品说明书进行。所用试剂或仪器未注明生产厂商者,均为可通过市购到的常规产品。The following describes the embodiments of the present invention in detail, and those skilled in the art will understand that the following embodiments are intended to explain the present invention, and should not be regarded as limiting the present invention. Unless otherwise specified, in the following examples that do not explicitly describe specific techniques or conditions, those skilled in the art can carry out according to commonly used techniques or conditions in this field or according to product instructions. The reagents or instruments used were not indicated by the manufacturer, and they were all commercially available conventional products.
在本发明的一个方面,本发明提出了一种微生物燃料电池。参照图1~3,对本发明的微生物燃料电池进行详细的描述。In one aspect of the present invention, the present invention provides a microbial fuel cell. Referring to Figures 1 to 3, the microbial fuel cell of the present invention will be described in detail.
根据本发明的实施例,参照图1和图2,该微生物燃料电池100(图中未标出)包括:支撑骨架10,阴极层20,分隔膜30以及阳极层40。其中,支撑骨架10具有与外界连通的腔室11;阴极层20设置在支撑骨架10远离腔室11的一侧,并环绕支撑骨架10,且阴极层20由阴极材料形成;分隔膜30环绕阴极层20设置;而阳极层40环绕分隔膜30设置,阳极层40由阳极材料形成且负载有微生物。需要说明的是,本文中“外界”具体是指微生物燃料电池以外的空间,而“腔室”具体是指支撑骨架中心的中空结构。According to an embodiment of the present invention, referring to FIG. 1 and FIG. 2 , the microbial fuel cell 100 (not shown in the figure) includes: a supporting frame 10 , a cathode layer 20 , a separation membrane 30 and an anode layer 40 . Wherein, the support frame 10 has a chamber 11 communicating with the outside world; the cathode layer 20 is arranged on the side of the support frame 10 away from the chamber 11, and surrounds the support frame 10, and the cathode layer 20 is formed by a cathode material; the separator 30 surrounds the cathode The layer 20 is provided; and the anode layer 40 is provided around the separation membrane 30, the anode layer 40 is formed of an anode material and is loaded with microorganisms. It should be noted that the "outside" herein specifically refers to the space outside the microbial fuel cell, and the "chamber" specifically refers to the hollow structure supporting the center of the framework.
本发明的发明人在研究过程中发现,该微生物燃料电池在工作时,污水经位于外侧的阳极层40、分隔膜30和阴极层20,最终由中空的支撑骨架10流出。工作过程中可将微生物分解污水中COD的过程与水过滤过程进行结合起来,阳极层40负载有的产电微生物还可将污水中有机物氧化,产生电子并被阴极层20接收从而完成还原半反应。如此,在净化污水的同时,该微生物燃料电池还可有效地产电,并能处理高浓度有机废水,而且该微生物燃料电池的耐冲击负荷能力高;还可作为污水处理装置的核心组装到污水处理装置中,从而具有模块化的特征,易于应用到不同规模的污水处理装置,利于反应器的放大与规模化。The inventors of the present invention discovered during the research process that when the microbial fuel cell is working, the sewage flows through the outer anode layer 40 , separation membrane 30 and cathode layer 20 , and finally flows out from the hollow support frame 10 . During the working process, the microbial decomposition process of COD in sewage can be combined with the water filtration process. The electricity-producing microorganisms loaded on the anode layer 40 can also oxidize the organic matter in the sewage, generate electrons and be received by the cathode layer 20 to complete the reduction half-reaction . In this way, while purifying sewage, the microbial fuel cell can also effectively generate electricity, and can treat high-concentration organic wastewater, and the microbial fuel cell has a high impact load resistance; it can also be used as the core of a sewage treatment device and assembled to sewage treatment In the device, it has the characteristics of modularization, and is easy to apply to sewage treatment devices of different scales, which is beneficial to the enlargement and scale of the reactor.
根据本发明的实施例,分隔膜30的具体材料不受特别的限制,只要该材料组成的分隔膜30能有效地促进该微生物燃料电池对污水的过滤效果即可,本领域技术人员可根据待净化处理的污水中含有的物质进行选择。在本发明的一些实施例中,分隔膜30可选自玻璃纤维、滤布、塑料网、尼龙布、阳离子交换膜和阴离子交换膜的至少之一。如此,采用上述种类的材料,可进一步提高该微生物燃料电池的污水处理效果和产电效率。According to the embodiment of the present invention, the specific material of the separation membrane 30 is not particularly limited, as long as the separation membrane 30 composed of the material can effectively promote the filtration effect of the microbial fuel cell to sewage, those skilled in the art can according to the The substances contained in the purified sewage are selected. In some embodiments of the present invention, the separation membrane 30 can be selected from at least one of glass fiber, filter cloth, plastic mesh, nylon cloth, cation exchange membrane and anion exchange membrane. In this way, the use of the above-mentioned materials can further improve the sewage treatment effect and power generation efficiency of the microbial fuel cell.
根据本发明的实施例,支撑骨架10的具体材料不受特别的限制,只要该材料组成的支撑骨架10能有效地为该微生物燃料电池提供内部支撑即可,本领域技术人员可根据该微生物燃料电池的具体使用要求进行选择。在本发明的一些实施例中,支撑骨架10的材质可选择聚氯乙烯(PVC),如此,采用上述材料的支撑骨架10既可满足内部支撑的要求,从而使该微生物燃料电池的耐冲击负荷能力更好,且制造成本低,具有工业批量化生产的潜力。在本发明的一些具体示例中,支撑骨架10还可以是镂空的内部结构,如此,在保持支撑骨架10的支撑作用的同时,还可增加该微生物燃料电池的净水效率。According to the embodiment of the present invention, the specific material of the supporting frame 10 is not particularly limited, as long as the supporting frame 10 composed of the material can effectively provide internal support for the microbial fuel cell, those skilled in the art can according to the microbial fuel cell Choose according to the specific requirements of the battery. In some embodiments of the present invention, the material of the support frame 10 can be selected from polyvinyl chloride (PVC). Like this, the support frame 10 adopting the above-mentioned material can meet the requirements of internal support, thereby making the impact load resistance of the microbial fuel cell The ability is better, and the manufacturing cost is low, and it has the potential of industrial batch production. In some specific examples of the present invention, the supporting frame 10 can also be a hollowed-out inner structure, so that while maintaining the supporting function of the supporting frame 10, the water purification efficiency of the microbial fuel cell can also be increased.
根据本发明的实施例,支撑骨架10的具体形状也不受特别的限制,只要该形状的支撑骨架10能有效地为该微生物燃料电池提供内部支撑即可,本领域技术人员可根据实际情况进行设计。在本发明的一些实施例中,支撑骨架10可包括中心环部分和底座部分,其中,中心环部分为整个微生物燃料电池提供侧向的支撑力,而底座部分为其他各层提供垂直方向上的支撑力的同时还可组装到污水处理装置上。According to the embodiment of the present invention, the specific shape of the supporting frame 10 is not particularly limited, as long as the supporting frame 10 of this shape can effectively provide internal support for the microbial fuel cell, those skilled in the art can make according to the actual situation. design. In some embodiments of the present invention, the supporting frame 10 may include a central ring part and a base part, wherein the central ring part provides lateral support for the entire microbial fuel cell, and the base part provides vertical support for other layers. It can also be assembled to the sewage treatment device while supporting the force.
根据本发明的实施例,形成阴极层20的阴极材料的具体种类,不受特别的限制,本领域技术人员可根据该微生物燃料电池的具体反应类型进行选择。在本发明的一些实施例中,阴极材料可以选自活性炭颗粒、石墨颗粒和碳纤维布的至少之一。如此,采用上述材料种类的阴极层20,能有效地接收电子,从而使该微生物燃料电池的产电效率更高。According to the embodiment of the present invention, the specific type of cathode material forming the cathode layer 20 is not particularly limited, and those skilled in the art can select according to the specific reaction type of the microbial fuel cell. In some embodiments of the present invention, the cathode material may be selected from at least one of activated carbon particles, graphite particles and carbon fiber cloth. In this way, the cathode layer 20 using the above-mentioned types of materials can effectively receive electrons, so that the efficiency of electricity production of the microbial fuel cell is higher.
根据本发明的实施例,阴极层20的具体结构不受特别的限制,本领域技术人员可根据阴极材料的具体种类进行设计。在本发明的一些实施例中,参照图3,阴极层20可进一步包括第一阴极集电网21和第二阴极集电网22,且第一阴极集电网21和第二阴极集电网22分别设置在阴极材料的两侧。如此,在阴极材料两侧分别设置的集电网,可将阴极层20接收的电子汇集给污水处理装置的电能回收单元,从而有效地收集和利用该微生物燃料电池在净化污水同时产生的电能。According to the embodiment of the present invention, the specific structure of the cathode layer 20 is not particularly limited, and those skilled in the art can design according to the specific type of cathode material. In some embodiments of the present invention, referring to FIG. 3, the cathode layer 20 may further include a first cathode collector network 21 and a second cathode collector network 22, and the first cathode collector network 21 and the second cathode collector network 22 are respectively arranged on both sides of the cathode material. In this way, the collector grids provided on both sides of the cathode material can collect the electrons received by the cathode layer 20 to the electric energy recovery unit of the sewage treatment device, thereby effectively collecting and utilizing the electric energy generated by the microbial fuel cell while purifying sewage.
根据本发明的实施例,形成阳极层40的阳极材料的具体种类,不受特别的限制,只要该种类材料形成的阳极层40可负载产电微生物即可,本领域技术人员可根据负载的微生物的具体类型进行选择。在本发明的一些实施例中,阳极材料可选自活性炭颗粒、石墨颗粒和碳纤维布的至少之一。如此,采用上述材料种类的阳极层40,能有效地负载产电微生物,从而使该微生物燃料电池的污水处理效果更好。According to the embodiment of the present invention, the specific type of anode material forming the anode layer 40 is not particularly limited, as long as the anode layer 40 formed by this type of material can support electrogenic microorganisms, those skilled in the art can select according to the microorganisms loaded. specific type of selection. In some embodiments of the present invention, the anode material may be selected from at least one of activated carbon particles, graphite particles and carbon fiber cloth. In this way, the use of the anode layer 40 of the above materials can effectively support the microorganisms producing electricity, so that the sewage treatment effect of the microbial fuel cell is better.
根据本发明的实施例,阳极层40的具体结构不受特别的限制,本领域技术人员可根据阴极材料的具体种类进行设计。在本发明的一些实施例中,参照图3,阳极层40可进一步包括第一阳极集电网41以及第二阳极集电网42,且第一阳极集电网41和第二阳极集电网42分别设置在阴极材料的两侧。如此,在阳极材料两侧分别设置的集电网,可将阳极层40与污水处理装置的电能回收单元相连,从而有效地利用该微生物燃料电池在净化污水同时产生的电能。According to the embodiment of the present invention, the specific structure of the anode layer 40 is not particularly limited, and those skilled in the art can design according to the specific type of cathode material. In some embodiments of the present invention, referring to FIG. 3 , the anode layer 40 may further include a first anode collector grid 41 and a second anode collector grid 42, and the first anode collector grid 41 and the second anode collector grid 42 are respectively arranged on both sides of the cathode material. In this way, the collector grids respectively arranged on both sides of the anode material can connect the anode layer 40 with the electric energy recovery unit of the sewage treatment device, thereby effectively utilizing the electric energy generated by the microbial fuel cell while purifying sewage.
根据本发明的实施例,第一阴极集电网21、第二阴极集电网22、第一阳极集电网41和第二阳极集电网42的具体材料,均不受特别的限制,本领域技术人员可根据阴极层20和阳极层40的具体材料尺寸以及该微生物燃料电池的耐冲击负荷性能要求进行选择。在本发明的一些实施例中,上述的各个集电网可独立地选择钛网或不锈钢网。如此,采用上述材料的集电网,可使该微生物燃料电池具有更好的耐冲击负荷能力。According to the embodiment of the present invention, the specific materials of the first cathode collector grid 21, the second cathode collector grid 22, the first anode collector grid 41 and the second anode collector grid 42 are not particularly limited, and those skilled in the art can The selection is made according to the specific material size of the cathode layer 20 and the anode layer 40 and the requirement of the microbial fuel cell's impact load resistance performance. In some embodiments of the present invention, titanium mesh or stainless steel mesh can be selected independently for each of the above-mentioned collector meshes. In this way, the use of the collecting grid of the above materials can make the microbial fuel cell have better impact load resistance.
根据本发明的实施例,参照图3,该微生物燃料电池还可以进一步包括支撑层50。其中,支撑层50设置在第二阳极集流网42的外壁,且该支撑层50可为钛网或不锈钢网。如此,采用上述材料的支撑层50,可使该微生物燃料电池具有更好的耐冲击负荷能力和结构稳定性。According to an embodiment of the present invention, referring to FIG. 3 , the microbial fuel cell may further include a support layer 50 . Wherein, the supporting layer 50 is arranged on the outer wall of the second anode current collecting net 42 , and the supporting layer 50 can be a titanium mesh or a stainless steel mesh. In this way, the use of the support layer 50 of the above materials can make the microbial fuel cell have better impact load resistance and structural stability.
根据本发明的实施例,该微生物燃料横截面的具体形状不受特别的限制,具体例如圆形、方形等,本领域技术人员根据该微生物燃料电池的使用环境进行设计。在本发明的一些实施例中,参照图1,该微生物燃料横截面外形可以为圆形,如此,各层在不同位置的厚度均匀,且各处的污水处理效果更均匀。According to the embodiment of the present invention, the specific shape of the cross-section of the microbial fuel is not particularly limited, such as circular, square, etc., and those skilled in the art can design it according to the environment in which the microbial fuel cell is used. In some embodiments of the present invention, referring to FIG. 1 , the cross-sectional shape of the microbial fuel can be circular, so that the thickness of each layer at different positions is uniform, and the sewage treatment effect is more uniform everywhere.
根据本发明的实施例,该微生物燃料的具体高度也不受特别的限制,本领域技术人员可根据组装有该微生物燃料的污水处理装置的尺寸进行设计和调整,在此不再赘述。根据本发明的实施例,该微生物燃料的各层结构(包括支撑骨架、阴极层、分隔层、阳极层和支撑层)的具体厚度也不受特别的限制,本领域技术人员可根据实际净水效果和产电效率进行设计和调整,在此不再赘述。According to the embodiment of the present invention, the specific height of the microbial fuel is not particularly limited, and those skilled in the art can design and adjust it according to the size of the sewage treatment device assembled with the microbial fuel, and details will not be repeated here. According to the embodiment of the present invention, the concrete thickness of each layer structure (comprising support frame, cathode layer, separation layer, anode layer and support layer) of this microbial fuel is not particularly limited, those skilled in the art can according to actual water purification The effect and power generation efficiency are designed and adjusted, and will not be repeated here.
综上所述,根据本发明的实施例,本发明提出了一种微生物燃料电池,具有以下益处:In summary, according to the embodiments of the present invention, the present invention proposes a microbial fuel cell, which has the following benefits:
1.该微生物燃料电池,具有模块化的特征,易于应用于不同规模的污水处理装置,利于反应器的放大与规模化;1. The microbial fuel cell has the characteristics of modularization and is easy to be applied to sewage treatment devices of different scales, which is beneficial to the enlargement and scale of the reactor;
2.该微生物燃料电池,易于搭建组装,并易于根据水质特征进行阴阳极选材与尺寸的进行调整;2. The microbial fuel cell is easy to build and assemble, and it is easy to adjust the material selection and size of the cathode and anode according to the water quality characteristics;
3.该微生物燃料电池,其组成材料来源广泛且成本较低,大大降低生物电化学系统的成本,有助于推广使用。3. The microbial fuel cell has a wide range of constituent materials and low cost, which greatly reduces the cost of the bioelectrochemical system and is helpful for popularization and use.
在本发明的另一个方面,本发明提出了一种污水处理装置。参照图4~7,对本发明的污水处理装置进行详细的描述。In another aspect of the present invention, the present invention provides a sewage treatment device. Referring to Figures 4-7, the sewage treatment device of the present invention will be described in detail.
根据本发明的实施例,参照图4,该污水处理装置包括:污水处理单元200,进水单元300,出水单元400以及电能回收单元500。其中,污水处理单元200包括至少一个上述的微生物燃料电池100;进水单元300用于向污水处理单元200供给污水;出水单元400与污水处理单元200相连,用于收集微生物燃料电池100过滤后的水;而电能回收单元500与污水处理单元200相连。According to an embodiment of the present invention, referring to FIG. 4 , the sewage treatment device includes: a sewage treatment unit 200 , a water inlet unit 300 , a water outlet unit 400 and an electric energy recovery unit 500 . Wherein, the sewage treatment unit 200 includes at least one above-mentioned microbial fuel cell 100; the water inlet unit 300 is used to supply sewage to the sewage treatment unit 200; water; and the electric energy recovery unit 500 is connected with the sewage treatment unit 200 .
本发明的发明人在研究过程中发现,该污水处理装置包括了进水单元300、微生物燃料电池100、出水单元400和电能回收单元500,其构造紧凑简约,易于实现装置构型的放大;作为一种模块化、组件式的污水处理与能量回收利用装置,具有低能耗、耐冲击负荷、可利用污水化学能产生电能等特点,既可以用于生活污水的处理,也可用于工业废水的处理。The inventors of the present invention discovered during the research process that the sewage treatment device includes a water inlet unit 300, a microbial fuel cell 100, a water outlet unit 400, and an electric energy recovery unit 500, and its structure is compact and simple, and it is easy to realize the enlargement of the device configuration; as A modular and component-type sewage treatment and energy recovery device, which has the characteristics of low energy consumption, impact load resistance, and the ability to use sewage chemical energy to generate electricity. It can be used for both domestic sewage treatment and industrial wastewater treatment .
根据本发明的实施例,参照图5,该污水处理装置进一步包括:曝气单元600,曝气单元600的至少一部分设置在微生物燃料电池100的阴极层内,用于向阴极层提供好氧环境。如此,污水依次经过厌氧(进水单元300)-厌氧(微生物燃料电池100的阳极层40)-好氧(微生物燃料电池100的阴极层20及中心好氧区),从而形成膜生物电化学强化的厌氧-厌氧-好氧(AAO)处理模式。在本发明的一些实施例中,曝气单元600可以包括至少一根穿孔管,该穿孔管可内嵌在阴极层20中,向阴极层20中提供更均匀的好氧环境。在本发明的一些具体示例中,穿孔管还可内嵌并环绕于阴极层20中,从而进一步向阴极层20中提供更均匀的好氧环境。According to an embodiment of the present invention, with reference to Fig. 5, the sewage treatment device further includes: an aeration unit 600, at least a part of the aeration unit 600 is arranged in the cathode layer of the microbial fuel cell 100, for providing an aerobic environment to the cathode layer . In this way, sewage sequentially passes through anaerobic (inlet unit 300)-anaerobic (anode layer 40 of microbial fuel cell 100)-aerobic (cathode layer 20 of microbial fuel cell 100 and central aerobic zone), thereby forming a membrane bioelectricity. Chemically enhanced anaerobic-anaerobic-aerobic (AAO) treatment mode. In some embodiments of the present invention, the aeration unit 600 may include at least one perforated tube, and the perforated tube may be embedded in the cathode layer 20 to provide a more uniform aerobic environment in the cathode layer 20 . In some specific examples of the present invention, the perforated tube can also be embedded and surrounded in the cathode layer 20 , so as to further provide a more uniform aerobic environment in the cathode layer 20 .
根据本发明的实施例,该污水处理单元200包括多个微生物燃料电池100。需要说明的是,本文中的所有“多个”是指两个或两个以上。在本发明的一些实施例中,污水处理单元200可包括6个微生物燃料电池100。According to an embodiment of the present invention, the sewage treatment unit 200 includes a plurality of microbial fuel cells 100 . It should be noted that all "plurality" herein refers to two or more. In some embodiments of the present invention, the sewage treatment unit 200 may include six microbial fuel cells 100 .
根据本发明的实施例,多个微生物燃料电池100之间水路的具体连接模式,不受特别的限制,本领域技术人员可根据该污水处理装置的污水处理量要求和净水效果标准进行设计和连接。例如,多个微生物燃料电池100之间的水路可采用并联模式或串联模式。需要说明的是,在本申请中,“多个微生物燃料电池之间的水路”即污水流经多个微生物燃料电池100的通路,“串联模式”即污水流经一个微生物燃料电池100之后,再经过第二个微生物燃料电池100进行处理;“并联模式”即污水同时流经多个微生物燃料电池100。采用串联模式的多个微生物燃料电池100可以提高该污水处理单元200处理污水的效率,采用并联模式的多个微生物燃料电池100可以提高该污水处理单元200的污水处理量。并且,根据本发明的实施例,污水处理单元200中的多个微生物燃料电池100,还可以同时采用串联以及并联的模式设置,由此,有利于进一步提高该污水处理单元200的处理效果。According to the embodiment of the present invention, the specific connection mode of the waterways between the multiple microbial fuel cells 100 is not particularly limited, and those skilled in the art can design and implement according to the sewage treatment capacity requirements and water purification effect standards of the sewage treatment device. connect. For example, the waterways between multiple microbial fuel cells 100 can be connected in parallel or in series. It should be noted that, in this application, "a waterway between multiple microbial fuel cells" refers to the passage through which sewage flows through multiple microbial fuel cells 100, and "series mode" refers to the sewage flowing through one microbial fuel cell 100, and then The second microbial fuel cell 100 is used for treatment; "parallel mode" means that the sewage flows through multiple microbial fuel cells 100 at the same time. Using multiple microbial fuel cells 100 in series mode can improve the sewage treatment efficiency of the sewage treatment unit 200 , and using multiple microbial fuel cells 100 in parallel mode can increase the sewage treatment capacity of the sewage treatment unit 200 . Moreover, according to the embodiment of the present invention, the plurality of microbial fuel cells 100 in the sewage treatment unit 200 can also be set in series and parallel mode at the same time, thereby further improving the treatment effect of the sewage treatment unit 200 .
在本发明的一些具体示例中,参照图6,多个微生物燃料电池100之间的水路可采用并联模式。具体的,参照图5~7,进水单元300可进一步包括配水槽310配水槽堰板3110;当污水进入进水单元300后先流入配水槽310中,再经过如图8所示配水槽堰板3110的多个孔均匀分配污水后,流入污水处理单元200进行净化和发电;当污水透过微生物燃料电池100的净化处理后,从污水处理单元200流入并汇聚到出水单元400中。如此,将多个微生物燃料电池100并联使用,可大通量地高效处理高浓度有机废水,利于污水处理装置的放大使用与规模化处理,且发电效率更高。In some specific examples of the present invention, referring to FIG. 6 , the water paths between multiple microbial fuel cells 100 can be connected in parallel. Specifically, referring to Figures 5-7, the water inlet unit 300 may further include a water distribution tank 310 and a water distribution tank weir plate 3110; After the multiple holes of the plate 3110 evenly distribute the sewage, it flows into the sewage treatment unit 200 for purification and power generation; In this way, using multiple microbial fuel cells 100 in parallel can efficiently treat high-concentration organic wastewater with a large throughput, which is beneficial to the enlarged use and large-scale treatment of sewage treatment devices, and has higher power generation efficiency.
根据本发明的实施例,该污水处理装置可包括多个污水处理单元200,如此可更有效地处理大通量的有机废水或者将高浓度有机废水的净化效果更好。在本发明的一些具体示例中,多个污水处理单元200之间可串联设置。如此,可将多个污水处理单元200串联使用,从而可使该污水处理装置对高浓度有机污水净化处理的效果更佳。在本发明的另一些具体示例中,多个污水处理单元200之间还可采用多级运行模式。如此,将采用多级运行模式设置多个污水处理单元200,可使该污水处理装置的净化处理效果与发电效率都更加好。According to an embodiment of the present invention, the sewage treatment device may include a plurality of sewage treatment units 200, so that large-flux organic wastewater can be treated more effectively or high-concentration organic wastewater can be purified better. In some specific examples of the present invention, multiple sewage treatment units 200 may be arranged in series. In this way, a plurality of sewage treatment units 200 can be used in series, so that the sewage treatment device can better purify and treat high-concentration organic sewage. In other specific examples of the present invention, multiple sewage treatment units 200 may also adopt a multi-stage operation mode. In this way, a plurality of sewage treatment units 200 will be set in a multi-stage operation mode, which can improve the purification treatment effect and power generation efficiency of the sewage treatment device.
根据本发明的实施例,电能回收单元500可以包括电连接照明系统或电能存储系统。如此,可使该污水处理装置充分利用污水化学能产生电能,从而实现该装置的多功能化和低能耗的优势。According to an embodiment of the present invention, the electric energy recovery unit 500 may include an electrically connected lighting system or an electric energy storage system. In this way, the sewage treatment device can make full use of the chemical energy of sewage to generate electric energy, thereby realizing the advantages of multi-functionality and low energy consumption of the device.
根据本发明的实施例,还可以给微生物燃料电池100外加电源,如此可进一步提高提高每个微生物燃料电池100的净水效果和净水效率,从而使该污水处理装置处理高浓度工业废水的净水效果和净水效率都显著提升。According to the embodiment of the present invention, an external power supply can also be added to the microbial fuel cell 100, so that the water purification effect and water purification efficiency of each microbial fuel cell 100 can be further improved, so that the sewage treatment device can treat high-concentration industrial wastewater. Both water effect and water purification efficiency have been significantly improved.
综上所述,根据本发明的实施例,本发明提出了一种污水处理装置,具有以下益处:In summary, according to the embodiments of the present invention, the present invention proposes a sewage treatment device, which has the following benefits:
1.本发明实施例的污水处理装置,其构型与传统的单室型、双室型、管式等生物电化学系统构型相比,具有易于放大、适用处理规模广的特点,利于处理实际污废水。1. Compared with the traditional single-chamber, double-chamber, tubular and other bioelectrochemical system configurations, the sewage treatment device of the embodiment of the present invention has the characteristics of being easy to scale up and applicable to a wide range of treatment, which is beneficial to the treatment actual waste water.
2.本发明实施例的污水处理装置,与传统污水处理系统相比,其能耗低且在处理污水的同时,可以直接将污水中的化学能转化为电能,并可以实现电能的原位利用强化污水处理。2. Compared with the traditional sewage treatment system, the sewage treatment device of the embodiment of the present invention has low energy consumption and can directly convert the chemical energy in the sewage into electric energy while treating sewage, and can realize the in-situ utilization of electric energy Strengthen sewage treatment.
3.本发明实施例的污水处理装置,与传统污水处理系统相比,其具有更高的耐冲击负荷能力,可以用于高浓度有机废水的处理,也可利用阴极的还原过程阳极的氧化过程,处理难降解有机废水。3. Compared with the traditional sewage treatment system, the sewage treatment device of the embodiment of the present invention has a higher impact load resistance, can be used for the treatment of high-concentration organic wastewater, and can also use the reduction process of the cathode and the oxidation process of the anode , Treatment of refractory organic wastewater.
下面参考具体实施例,对本发明进行描述,需要说明的是,这些实施例仅是描述性的,而不以任何方式限制本发明。The present invention will be described below with reference to specific embodiments. It should be noted that these embodiments are only illustrative and do not limit the present invention in any way.
实施例1Example 1
在该实施例中,组装并其使用微生物燃料电池和污水处理装置。具体如下:In this example, a microbial fuel cell and a sewage treatment device were assembled and used. details as follows:
(1)微生物燃料电池的构建:该组件高为1米,直径为155mm圆筒形,从内而外依次为支撑骨架、阴极层(含曝气系统)、分隔层、阳极层与支撑层。其中,支撑骨架的材质为PVC,其底座直径为155mm圆盘,其中心为25mm直径圆形出水口,其主体为直径89mm高1000mm骨架,镂空,开孔面积约50%。阴极层的厚度约18mm,内外侧采用50目钛网集电,中间填充颗粒炭,且填充质量约为2.5kg,并且阴极层内嵌曝气系统,6mm直径穿孔管内嵌环绕于阴极层。分隔层采用滤布与塑料网支撑。阳极层的厚约10mm,内外侧采用50目的钛网集电,中间填充颗粒炭,且填充质量约为2.5kg。而支撑层,与阳极外侧集电层合并。(1) Construction of microbial fuel cell: the component is 1 meter high and 155 mm in diameter cylindrical, from the inside to the outside are the support frame, cathode layer (including aeration system), separation layer, anode layer and support layer. Among them, the supporting frame is made of PVC, its base is a disc with a diameter of 155mm, and its center is a circular water outlet with a diameter of 25mm. The main body is a skeleton with a diameter of 89mm and a height of 1000mm. The thickness of the cathode layer is about 18mm. The inner and outer sides are collected by 50-mesh titanium mesh, and the middle is filled with granular carbon, and the filling quality is about 2.5kg. The cathode layer is embedded with an aeration system, and a 6mm diameter perforated tube is embedded and surrounds the cathode layer. The separation layer is supported by filter cloth and plastic mesh. The thickness of the anode layer is about 10mm, the inner and outer sides are collected by 50-mesh titanium mesh, and the middle is filled with granular carbon, and the filling quality is about 2.5kg. The supporting layer is combined with the outer collector layer of the anode.
(2)污水处理装置:包含上述6组微生物燃料电池的污水处理装置,还包括进水单元、出水单元和电能回收单元。该装置平面为矩形,长2400mm,宽1200mm,微生物燃料电池高为1440mm,出水汇集单元高300mm。而微生物燃料电池之间水路采用并联模式,即上层中心为配水槽,堰板分布有12个孔,直径20mm,用于均匀分配污水。阴极两个钛网用多组钛丝连接,阳极两个钛网用多组钛丝连接。阴极与阳极之间,连接外电阻5欧姆。(2) Sewage treatment device: a sewage treatment device including the above-mentioned 6 groups of microbial fuel cells, and also includes a water inlet unit, a water outlet unit and an electric energy recovery unit. The plane of the device is rectangular, with a length of 2400mm and a width of 1200mm. The height of the microbial fuel cell is 1440mm, and the height of the effluent collection unit is 300mm. The waterway between the microbial fuel cells adopts a parallel mode, that is, the center of the upper layer is a water distribution tank, and the weir plate is distributed with 12 holes with a diameter of 20mm for evenly distributing sewage. The two titanium meshes of the cathode are connected by multiple sets of titanium wires, and the two titanium meshes of the anode are connected by multiple sets of titanium wires. Between the cathode and the anode, connect an external resistor of 5 ohms.
(3)该实施例中,以煤化工煤制气废水为原水,使用了煤制气废水处理厂常用进水浓度2500-3000mg/L COD为初始运行条件,逐步提升进水浓度至9000mg/L COD,可保持较快速的COD降解速度,并可同时实现难降解污水产电。该实施例也是全球第一个应用于煤化工废水处理的微生物燃料电池中试装置。(3) In this example, coal chemical industry coal gas wastewater is used as raw water, and the influent concentration commonly used in coal gas wastewater treatment plants is 2500-3000mg/L COD as the initial operating condition, and the influent concentration is gradually increased to 9000mg/L COD can maintain a relatively fast COD degradation rate, and at the same time realize the power generation of refractory sewage. This example is also the world's first microbial fuel cell pilot plant applied to coal chemical wastewater treatment.
该实施例的废水处理和产电的结果,如图8~10所示。The results of wastewater treatment and electricity generation in this embodiment are shown in Figures 8-10.
该实施例的污水处理装置处理煤制气废水COD的情况,如图8所示。从图8可看出,当第一个处理周期中,向该污水处理装置加入COD为3000mg/L的污水,经过200小时循环处理后COD降至1000mg/L以下;当第二个处理周期中,向该污水处理装置加入COD为4000mg/L的污水,经过200小时循环处理后COD降至1000mg/L左右;当第三个处理周期中,向该污水处理装置加入COD为5000mg/L的污水,经过100小时循环处理后COD降至2000mg/L以下;当第四个处理周期中,向该污水处理装置加入COD为9000mg/L的污水,经过200小时循环处理后COD降至3000mg/L以下。通过实验结果可说明,虽然每个微生物燃料电池的填充量少,仍旧可以适用于处理高COD浓度的煤制气废水,且处理煤制气废水的效果较好。The sewage treatment device of this embodiment treats the COD of coal-gas wastewater, as shown in FIG. 8 . It can be seen from Figure 8 that when the first treatment cycle is added to the sewage treatment plant with sewage with a COD of 3000 mg/L, the COD drops below 1000 mg/L after 200 hours of circulating treatment; , add sewage with a COD of 4000mg/L to the sewage treatment plant, and after 200 hours of circulating treatment, the COD will drop to about 1000mg/L; in the third treatment cycle, add sewage with a COD of 5000mg/L to the sewage treatment plant , COD drops below 2000mg/L after 100 hours of circulating treatment; in the fourth treatment cycle, add sewage with COD of 9000mg/L to the sewage treatment plant, after 200 hours of circulating treatment, COD drops below 3000mg/L . The experimental results show that although the filling amount of each microbial fuel cell is small, it can still be applied to the treatment of coal-to-gas wastewater with high COD concentration, and the treatment effect of coal-to-gas wastewater is better.
该实施例的污水处理装置处理煤制气废水的同步产电情况,如图9所示。从图9可看出,该污水处理装置在处理污水的同时,产电电流也比较理想。The synchronous power generation of the sewage treatment device in this embodiment to treat the coal-to-gas wastewater is shown in FIG. 9 . It can be seen from Fig. 9 that the sewage treatment device can also generate electricity more ideally while treating sewage.
该污水处理装置的处理煤制气废水同步产电功率,如图10所示。具体的,将外阻设置为1000欧姆并稳定运行1~2小时后,每十分钟更换一次外阻并测出相应地功率,其中,外阻分别为500、300、200、150、100、50、30、20、15、10、5、3、2和1欧姆。从图10可看出,该污水处理装置的产电功率高,并且与5欧姆的外阻相比该污水处理装置本身的内阻较小。The sewage treatment device treats the coal-to-gas wastewater and simultaneously generates power, as shown in Figure 10. Specifically, after setting the external resistance to 1000 ohms and running it stably for 1 to 2 hours, replace the external resistance every ten minutes and measure the corresponding power, where the external resistances are 500, 300, 200, 150, 100, 50 , 30, 20, 15, 10, 5, 3, 2 and 1 ohms. It can be seen from Fig. 10 that the power generation power of the sewage treatment device is high, and the internal resistance of the sewage treatment device itself is smaller than the external resistance of 5 ohms.
实施例2Example 2
在该实施例中,按照实施例1基本相同的方法和条件,组装并其使用微生物燃料电池和污水处理装置。区别在于,在该实施例中:In this example, the microbial fuel cell and the sewage treatment device were assembled and used according to the same method and conditions as in Example 1. The difference is that, in this example:
(1)微生物燃料电池的构建:支撑层选择钛网;阳极层采用石墨颗粒;分隔层采用尼龙布;阴极层采用石墨颗粒;曝气单元可将穿孔管置于阴极层外侧接近中心区域。(1) Construction of microbial fuel cell: Titanium mesh is selected for the support layer; graphite particles are used for the anode layer; nylon cloth is used for the separation layer; graphite particles are used for the cathode layer;
其他均和实施例1一样。Others are all the same as in Example 1.
实施例3Example 3
在该实施例中,按照实施例1基本相同的方法和条件,组装并其使用微生物燃料电池和污水处理装置。区别在于,在该实施例中,6个微生物燃料电池之间水路采用串联模式。In this example, the microbial fuel cell and the sewage treatment device were assembled and used according to the same method and conditions as in Example 1. The difference is that in this embodiment, the waterways between the six microbial fuel cells are connected in series.
实施例4Example 4
在该实施例中,按照实施例1基本相同的方法和条件,组装并其使用微生物燃料电池和污水处理装置。区别在于,在该实施例中,污水处理装置包括2个污水处理单元,且2个污水处理单元之间串联设置,而每个污水处理单元中6个微生物燃料电池之间水路采用并联模式。In this example, the microbial fuel cell and the sewage treatment device were assembled and used according to the same method and conditions as in Example 1. The difference is that in this embodiment, the sewage treatment device includes 2 sewage treatment units, and the 2 sewage treatment units are arranged in series, and the waterways between the 6 microbial fuel cells in each sewage treatment unit are in parallel mode.
实施例5Example 5
在该实施例中,按照实施例1基本相同的方法和条件,组装并其使用微生物燃料电池和污水处理装置。区别在于,在该实施例中,微生物燃料电池的阴极与阳极之间连接的是LED灯,即电能回收装置为LED灯,且经过升压模块,形成照明系统。In this example, the microbial fuel cell and the sewage treatment device were assembled and used according to the same method and conditions as in Example 1. The difference is that in this embodiment, LED lamps are connected between the cathode and anode of the microbial fuel cell, that is, the electric energy recovery device is an LED lamp, which forms a lighting system through a booster module.
实施例6Example 6
在该实施例中,按照实施例1基本相同的方法和条件,组装并其使用微生物燃料电池和污水处理装置。区别在于,在该实施例中,微生物燃料电池的阴极与阳极之间连接的是电容器以及电容器-电磁继电器模块,即电能回收装置为电容器,从而可实现电能存储的功能。In this example, the microbial fuel cell and the sewage treatment device were assembled and used according to the same method and conditions as in Example 1. The difference is that in this embodiment, a capacitor and a capacitor-electromagnetic relay module are connected between the cathode and the anode of the microbial fuel cell, that is, the electric energy recovery device is a capacitor, thereby realizing the function of electric energy storage.
总结Summarize
综合实施例1~6可得出,本发明所提出的微生物燃料电池以及污水处理装置。该微生物燃料电池作为污水处理装置的核心模块,在阳极层和阴极层之间增设的分隔膜,可有效地提高该微生物燃料电池的污水处理效果和产电效率,并能处理高浓度有机废水。该污水处理装置构造紧凑简约,易于实现装置构型的放大;作为一种模块化、组件式的污水处理与能量回收利用装置,具有低能耗、耐冲击负荷、可利用污水化学能产生电能等特点,既可以用于生活污水的处理,也可用于工业废水的处理。It can be concluded from comprehensive examples 1 to 6 that the microbial fuel cell and the sewage treatment device proposed by the present invention. The microbial fuel cell is used as the core module of the sewage treatment device. The separation membrane added between the anode layer and the cathode layer can effectively improve the sewage treatment effect and power generation efficiency of the microbial fuel cell, and can treat high-concentration organic wastewater. The structure of the sewage treatment device is compact and simple, and it is easy to realize the enlargement of the device configuration; as a modularized and componentized sewage treatment and energy recovery device, it has the characteristics of low energy consumption, impact load resistance, and the use of sewage chemical energy to generate electric energy, etc. , can be used not only for the treatment of domestic sewage, but also for the treatment of industrial wastewater.
在本发明的描述中,需要理解的是,术语“中心”、“纵向”、“横向”、“长度”、“宽度”、“厚度”、“上”、“下”、“前”、“后”、“左”、“右”、“竖直”、“水平”、“顶”、“底”、“内”、“外”、“顺时针”、“逆时针”、“轴向”、“径向”、“周向”等指示的方位或位置关系为基于附图所示的方位或位置关系,仅是为了便于描述本发明和简化描述,而不是指示或暗示所指的装置或元件必须具有特定的方位、以特定的方位构造和操作,因此不能理解为对本发明的限制。In describing the present invention, it should be understood that the terms "center", "longitudinal", "transverse", "length", "width", "thickness", "upper", "lower", "front", " Back", "Left", "Right", "Vertical", "Horizontal", "Top", "Bottom", "Inner", "Outer", "Clockwise", "Counterclockwise", "Axial" , "radial", "circumferential" and other indicated orientations or positional relationships are based on the orientations or positional relationships shown in the drawings, which are only for the convenience of describing the present invention and simplifying the description, rather than indicating or implying the referred device or Elements must have certain orientations, be constructed and operate in certain orientations, and therefore should not be construed as limitations on the invention.
在本发明的描述中,除非另有明确的规定和限定,术语“安装”、“相连”、“连接”、“固定”等术语应做广义理解,例如,可以是固定连接,也可以是可拆卸连接,或成一体;可以是机械连接,也可以是电连接;可以是直接相连,也可以通过中间媒介间接相连,可以是两个元件内部的连通或两个元件的相互作用关系。对于本领域的普通技术人员而言,可以根据具体情况理解上述术语在本发明中的具体含义。In the description of the present invention, terms such as "installation", "connection", "connection" and "fixation" should be interpreted in a broad sense unless otherwise clearly specified and limited. Disassembled connection, or integration; it can be mechanical connection or electrical connection; it can be direct connection or indirect connection through an intermediary, and it can be the internal communication of two components or the interaction relationship between two components. Those of ordinary skill in the art can understand the specific meanings of the above terms in the present invention according to specific situations.
此外,术语“第一”、“第二”仅用于描述目的,而不能理解为指示或暗示相对重要性或者隐含指明所指示的技术特征的数量。由此,限定有“第一”、“第二”的特征可以明示或者隐含地包括至少一个该特征。在本发明的描述中,“多个”的含义是至少两个,例如两个,三个等,除非另有明确具体的限定。In addition, the terms "first" and "second" are used for descriptive purposes only, and cannot be interpreted as indicating or implying relative importance or implicitly specifying the quantity of indicated technical features. Thus, the features defined as "first" and "second" may explicitly or implicitly include at least one of these features. In the description of the present invention, "plurality" means at least two, such as two, three, etc., unless otherwise specifically defined.
在本说明书的描述中,参考术语“一个实施例”、“一些实施例”、“示例”、“具体示例”、或“一些示例”等的描述意指结合该实施例或示例描述的具体特征、结构、材料或者特点包含于本发明的至少一个实施例或示例中。在本说明书中,对上述术语的示意性表述不必须针对的是相同的实施例或示例。而且,描述的具体特征、结构、材料或者特点可以在任一个或多个实施例或示例中以合适的方式结合。此外,在不相互矛盾的情况下,本领域的技术人员可以将本说明书中描述的不同实施例或示例以及不同实施例或示例的特征进行结合和组合。In the description of this specification, descriptions referring to the terms "one embodiment", "some embodiments", "example", "specific examples", or "some examples" mean that specific features described in connection with the embodiment or example , structure, material or feature is included in at least one embodiment or example of the present invention. In this specification, the schematic representations of the above terms are not necessarily directed to the same embodiment or example. Furthermore, the described specific features, structures, materials or characteristics may be combined in any suitable manner in any one or more embodiments or examples. In addition, those skilled in the art can combine and combine different embodiments or examples and features of different embodiments or examples described in this specification without conflicting with each other.
尽管上面已经示出和描述了本发明的实施例,可以理解的是,上述实施例是示例性的,不能理解为对本发明的限制,本领域的普通技术人员在本发明的范围内可以对上述实施例进行变化、修改、替换和变型。Although the embodiments of the present invention have been shown and described above, it can be understood that the above embodiments are exemplary and should not be construed as limiting the present invention, those skilled in the art can make the above-mentioned The embodiments are subject to changes, modifications, substitutions and variations.
Claims (9)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710500473.1A CN107180988B (en) | 2017-06-27 | 2017-06-27 | Microbial fuel cell and sewage treatment device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710500473.1A CN107180988B (en) | 2017-06-27 | 2017-06-27 | Microbial fuel cell and sewage treatment device |
Publications (2)
Publication Number | Publication Date |
---|---|
CN107180988A CN107180988A (en) | 2017-09-19 |
CN107180988B true CN107180988B (en) | 2023-08-25 |
Family
ID=59845340
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710500473.1A Active CN107180988B (en) | 2017-06-27 | 2017-06-27 | Microbial fuel cell and sewage treatment device |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107180988B (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108751640B (en) * | 2018-07-31 | 2023-08-18 | 浙江工商大学 | A system and method for in-situ sludge synchronous reduction and stabilization treatment |
CN111003794B (en) * | 2019-12-25 | 2022-10-04 | 广州市环境保护工程设计院有限公司 | Artificial wetland system for treating rural domestic sewage |
CN112820924A (en) * | 2021-01-07 | 2021-05-18 | 西安建筑科技大学 | Microbial fuel cell for nitrogen and phosphorus removal of sewage treatment plant and sewage treatment method |
CN113737210A (en) * | 2021-08-13 | 2021-12-03 | 中国科学院城市环境研究所 | Electrolytic cell structure for carbon dioxide electrolysis |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101317297A (en) * | 2005-09-28 | 2008-12-03 | 株式会社荏原制作所 | Biological power plant, and method of treating organic solid contaminant-containing waste, method of treating organic high molecular substance-containing liquid waste and method of treating organic su |
CN102381753A (en) * | 2011-09-26 | 2012-03-21 | 中国科学技术大学 | Bioelectrochemical film reactor device |
CN104064791A (en) * | 2014-02-26 | 2014-09-24 | 武汉科技大学 | Biological inverted-conversion reactor of microbial fuel cell, purification method of CO2 in gas and preparation method of CO2 biological synthetic fuel |
CN204424375U (en) * | 2015-02-15 | 2015-06-24 | 中国海洋大学 | The microbiological fuel cell of in-situ remediation of underground water azotate pollution |
-
2017
- 2017-06-27 CN CN201710500473.1A patent/CN107180988B/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101317297A (en) * | 2005-09-28 | 2008-12-03 | 株式会社荏原制作所 | Biological power plant, and method of treating organic solid contaminant-containing waste, method of treating organic high molecular substance-containing liquid waste and method of treating organic su |
CN102381753A (en) * | 2011-09-26 | 2012-03-21 | 中国科学技术大学 | Bioelectrochemical film reactor device |
CN104064791A (en) * | 2014-02-26 | 2014-09-24 | 武汉科技大学 | Biological inverted-conversion reactor of microbial fuel cell, purification method of CO2 in gas and preparation method of CO2 biological synthetic fuel |
CN204424375U (en) * | 2015-02-15 | 2015-06-24 | 中国海洋大学 | The microbiological fuel cell of in-situ remediation of underground water azotate pollution |
Non-Patent Citations (1)
Title |
---|
张潇源.空气型微生物燃料电池分隔材料、阴极及构型优化.中国博士学位论文全文数据库 工程科技Ⅱ辑.2013,(2013第7期),第8-10页,第60页. * |
Also Published As
Publication number | Publication date |
---|---|
CN107180988A (en) | 2017-09-19 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Mathuriya et al. | Architectural adaptations of microbial fuel cells | |
Abdallah et al. | Continuous and scalable applications of microbial fuel cells: a critical review | |
CN102381753B (en) | A bioelectrochemical membrane reactor device | |
CN107180988B (en) | Microbial fuel cell and sewage treatment device | |
CN103708622B (en) | Microbial fuel cell constructed wetland for efficiently treating organic sewage | |
CN106746230B (en) | electro-Fenton sewage treatment system and method based on power supply of arrayed wetland microbial fuel cells | |
CN104505529A (en) | Algae-bacteria synergistic ecological microbial fuel cell and method for using it to purify water and generate electricity | |
CN102723517B (en) | Microbial fuel cell with separation membrane and biological negative pole, and sewage treatment method | |
CN103094598B (en) | Integrated nitrification-denitrification microbial fuel cell | |
CN104118931B (en) | A kind of electricity biological coupling water cleaning systems and process for purifying water | |
CN105859024A (en) | Ag3PO4 Photocatalytic Coupled Constructed Wetland Microbial Battery System and Its Application | |
CN102701543B (en) | Water treatment device combining microbial fuel cells with membrane technology | |
CN103496789A (en) | Sewage treatment unit and method using bioelectrochemistry to aid membrane bioreactor | |
KR101528159B1 (en) | Hybrid reactor consisting of upflow anaerobic sludge blanket reactor and microbial fuel cell | |
CN107244733B (en) | Accelerating device for sewage and wastewater synergistic treatment | |
CN207199757U (en) | Microbiological fuel cell, sewage-treatment plant | |
CN106927577A (en) | A kind of ecological water purifying device and its method for administering black and odorous water | |
CN108075162A (en) | A kind of method using the electricity production decontamination of self-respiration type microbiological fuel cell | |
CN111370725A (en) | MFC system based on biodynamic membrane and enhanced electricity generation method | |
CN110818065A (en) | Method for electrochemically treating livestock and poultry breeding wastewater based on biological cathode microorganisms | |
CN114477421A (en) | Double-chamber continuous flow integrated coking wastewater treatment device and method | |
CN103739070A (en) | Low-energy-consumption municipal wastewater recycling method | |
CN102010034B (en) | Preparation device of ferron used for water treatment and application method thereof | |
CN109761339B (en) | Micro-ecological cycle switching type wastewater treatment microbial electrochemical system | |
CN206858281U (en) | A kind of ecological water purifying device for administering black and odorous water |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |