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JP5872148B2 - Biological treatment method and method for producing microorganism group-supporting carrier - Google Patents
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JP5872148B2 - Biological treatment method and method for producing microorganism group-supporting carrier - Google Patents

Biological treatment method and method for producing microorganism group-supporting carrier Download PDF

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JP5872148B2
JP5872148B2 JP2010241396A JP2010241396A JP5872148B2 JP 5872148 B2 JP5872148 B2 JP 5872148B2 JP 2010241396 A JP2010241396 A JP 2010241396A JP 2010241396 A JP2010241396 A JP 2010241396A JP 5872148 B2 JP5872148 B2 JP 5872148B2
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methane fermentation
methane
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JP2011224539A (en
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建吾 佐々木
建吾 佐々木
仁彦 森田
仁彦 森田
松本 伯夫
伯夫 松本
伸一 平野
伸一 平野
大村 直也
直也 大村
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Central Research Institute of Electric Power Industry
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    • 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
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Description

本発明は、生物学的処理方法並びに微生物群担持担体の作製方法に関する。さらに詳述すると、本発明は、メタン発酵処理等に代表される生物学的処理方法、並びに微生物群担持担体の作製方法に関する。   The present invention relates to a biological treatment method and a method for producing a microorganism group-supporting carrier. More specifically, the present invention relates to a biological treatment method represented by methane fermentation treatment and the like, and a method for producing a microorganism group-supporting carrier.

微生物を利用した物質処理方法や物質生産方法のような生物学的処理方法は、環境負荷が少なく、低コストに実施できる方法として近年注目が集められており、各種研究・開発が進められつつある。   Biological treatment methods such as substance treatment methods and substance production methods utilizing microorganisms have attracted attention in recent years as methods that have low environmental impact and can be implemented at low cost, and various research and development are being promoted. .

その代表的なものとして、生ゴミ等の有機性廃棄物をメタン発酵処理する技術が挙げられる。メタン発酵処理とは、有機性廃棄物を発酵液に投入し、嫌気性条件下でメタン生成菌等により発酵処理して有機性廃棄物をメタンガス等のバイオガスに分解する方法である。メタン発酵処理は、有機性廃棄物を大幅に減容できることから、近年の埋め立て処分地の逼迫の問題を解決することができ、しかもメタンガスをエネルギーとして回収できる極めて有益性の高い技術として注目されている。   A typical example is a technology for methane fermentation of organic waste such as garbage. The methane fermentation treatment is a method in which organic waste is introduced into a fermentation broth and subjected to fermentation treatment with an anaerobic condition using a methane-producing bacterium to decompose the organic waste into biogas such as methane gas. Since methane fermentation treatment can greatly reduce the volume of organic waste, it has been attracting attention as an extremely useful technology that can solve the recent problems of landfill disposal and that can recover methane gas as energy. Yes.

そこで、近年、メタン発酵処理に関する技術が各種提案されている。例えば、特許文献1では、生ごみ等の有機性廃棄物をメタン発酵法で効率的に処理するシステムとして、有機性廃棄物をペースト状に粉砕して、50〜60℃で大きな活性を示す高温メタン菌で処理するシステムが開示されている。具体的には、高温メタン菌が、36〜38℃の中温で活性が大きくなる中温菌に比べて2〜3倍の活性を持っていることを利用し、高温メタン菌でメタン発酵を行うことで分解速度の向上と消化率の向上を図るようにしている。   Therefore, in recent years, various technologies related to methane fermentation treatment have been proposed. For example, in Patent Document 1, as a system for efficiently treating organic waste such as garbage with a methane fermentation method, the organic waste is pulverized into a paste and heated at a high temperature of 50 to 60 ° C. A system for treating with methane bacteria is disclosed. Specifically, using the fact that thermophilic methane bacteria are 2-3 times more active than mesophilic bacteria whose activity is increased at medium temperatures of 36 to 38 ° C., methane fermentation is performed with high temperature methane bacteria In order to improve the decomposition rate and digestibility.

特開平10−137730号公報Japanese Patent Laid-Open No. 10-137730

一般に、微生物を利用して物質を変換(分解、酸化、還元等)により処理する場合、高負荷条件、例えば微生物により処理される被処理物の濃度が一定値以上の高濃度になると、微生物の機能が低下し、処理能力が低下してしまうことが知られている。メタン発酵処理においてもこのことは例外ではなく、有機物負荷速度や水理学的滞留時間が高い高負荷条件下では、メタン発酵槽の酸敗等が生じて、メタン発酵処理能が著しく低下する場合がある。このような状況に陥ると、メタン発酵槽を再生する必要が生じ、メタン発酵処理が滞ることになる。そこで、高負荷条件下においても処理能力を低下させることなく、連続して処理を行うことのできる方法の確立が望まれる。   In general, when a substance is processed by conversion (decomposition, oxidation, reduction, etc.) using microorganisms, if the concentration of an object to be processed that is processed by microorganisms reaches a certain level or higher, It is known that the function is lowered and the processing capacity is lowered. This is no exception in methane fermentation treatment, and under high load conditions with high organic matter loading rate and hydraulic residence time, methane fermentation tanks may suffer from rancidity and the like, and the methane fermentation treatment ability may be significantly reduced. . If it falls into such a situation, it will be necessary to reproduce | regenerate a methane fermentation tank, and a methane fermentation process will be overdue. Therefore, it is desired to establish a method capable of performing continuous processing without reducing processing capacity even under high load conditions.

本発明は、かかる要望に鑑みてなされたものであって、高負荷条件下においても優れた処理能力を発揮して効率よく実施することのできる生物学的処理方法を提供することを目的とする。   The present invention has been made in view of such demands, and an object of the present invention is to provide a biological treatment method that can be efficiently performed while exhibiting excellent treatment capacity even under high load conditions. .

また、本発明は、高負荷条件下においても優れた処理能力を発揮する微生物担持担体を作製する方法を提供することを目的とする。   Another object of the present invention is to provide a method for producing a microorganism-supporting carrier that exhibits excellent processing ability even under high load conditions.

かかる課題を解決するため、本願発明者等が鋭意検討を行ったところ、有機性廃棄物を発酵液に投入してメタン発酵を行うメタン発酵方法において、板状の炭素電極の片面に炭素繊維を備えた担体保持電極を有機性廃棄物と共に発酵液に接触させ、担体保持電極の電位を銀・塩化銀電極電位基準で−0.8V〜−1.0Vに制御しながらメタン発酵を行うことで、高負荷運転条件下においても優れたメタン発酵処理能力を発揮することを知見するに至った。   In order to solve such a problem, the inventors of the present application have made extensive studies, and in a methane fermentation method in which organic waste is introduced into a fermentation broth to perform methane fermentation, carbon fiber is provided on one side of a plate-like carbon electrode. By carrying the methane fermentation while bringing the carrier-supporting electrode provided into contact with the fermented liquid together with the organic waste, and controlling the potential of the carrier-holding electrode to -0.8 V to -1.0 V based on the silver / silver chloride electrode potential reference It has been found that it exhibits excellent methane fermentation treatment capacity even under high-load operation conditions.

本願発明者等は、これらの知見から、メタン発酵処理について、担体保持電極の電位を、担体保持電極から電子が供給される電位または銀・塩化銀電極電位基準で+0.3Vに制御することで、高負荷条件下においても優れた処理能力を発揮させて、効率よく実施することができる可能性が導かれることを知見し、本願発明を完成するに至った。 Based on these findings, the inventors of the present application controlled the potential of the carrier holding electrode to +0.3 V with respect to the potential at which electrons are supplied from the carrier holding electrode or the silver / silver chloride electrode potential for methane fermentation treatment. Thus, the inventors have found that the possibility of being able to be implemented efficiently by exhibiting excellent processing ability even under high load conditions has led to the completion of the present invention.

即ち、本発明のメタン発酵方法は、電極表面の少なくとも一部に疎水性の担体を備えた担体保持電極と有機性基質及びメタン発酵に関与する微生物群を含み且つ有機性基質をメタン発酵処理するメタン発酵液とを接触させ、担体保持電極の電位を担体保持電極から電子が供給される電位または銀・塩化銀電極電位基準で+0.3Vに制御しながらメタン発酵処理を行うようにしている。 That is, the methane fermentation process of the present invention is the methane fermentation processes and organic substrates include microorganisms involved in the carrier holding electrode and the organic substrate and methane fermentation with at least a part sparse aqueous carrier of the electrode surface The methane fermentation solution is brought into contact, and the methane fermentation treatment is performed while controlling the potential of the carrier holding electrode to +0.3 V based on the potential at which electrons are supplied from the carrier holding electrode or the silver / silver chloride electrode potential.

ここで、本発明のメタン発酵方法において、担体保持電極を作用電極とし、作用電極と対電極と参照電極とをポテンシオスタットに結線し、メタン発酵液と電解液とをイオン交換膜を介して接触させ、メタン発酵液に作用電極と参照電極とを接触させ、電解液に対電極を接触させ、作用電極の電位を3電極方式で制御することが好ましい。また、担体保持電極を作用電極とし、作用電極と対電極と参照電極とをポテンシオスタットに結線し、メタン発酵液と対電極とをイオン交換膜を介して接触させ、メタン発酵液に作用電極と参照電極とを接触させ、作用電極の電位を3電極方式で制御することが好ましい。この場合、担体保持電極の電位を、担体保持電極から電子が供給される電位である−0.8V〜−1.0V(銀・塩化銀電極電位基準)に制御することが好ましい。また、担体は炭素繊維であることが好ましい。 Here, in the methane fermentation method of the present invention, the carrier holding electrode is used as a working electrode, the working electrode, the counter electrode, and the reference electrode are connected to a potentiostat , and the methane fermentation solution and the electrolytic solution are connected via an ion exchange membrane. Preferably, the working electrode and the reference electrode are brought into contact with the methane fermentation solution, the counter electrode is brought into contact with the electrolytic solution, and the potential of the working electrode is controlled by a three-electrode system. In addition, the carrier holding electrode is used as a working electrode, the working electrode, the counter electrode, and the reference electrode are connected to a potentiostat , and the methane fermentation broth and the counter electrode are brought into contact with each other through an ion exchange membrane, so that the working electrode is in contact with the methane fermentation broth. And the reference electrode are brought into contact with each other, and the potential of the working electrode is preferably controlled by a three-electrode system. In this case, the potential of the carrier holding electrode is preferably controlled to -0.8 V to -1.0 V (silver / silver chloride electrode potential reference), which is a potential at which electrons are supplied from the carrier holding electrode. The carrier is preferably carbon fiber.

次に、本発明の微生物群担持担体の作製方法(微生物群が担持された担体の作製方法)は、電極表面の少なくとも一部に疎水性の担体を備えた担体保持電極と有機性基質及びメタン発酵に関与する微生物群を含み且つ有機性基質をメタン発酵処理するメタン発酵液とを接触させ、担体保持電極の電位を担体保持電極から電子が供給される電位または銀・塩化銀電極電位基準で+0.3Vに制御し、担体にメタン発酵に関与する微生物群を担持させて活性化させるようにしている。 Next, (a method for manufacturing a carrier microorganisms is carried) Preparation method of microorganisms supporting carrier of the present invention, the carrier holding electrode having at least a part hydrophobicity of the support surface of the electrode and the organic substrate and methane A methane fermentation solution containing a microorganism group involved in fermentation and containing an organic substrate for methane fermentation is brought into contact, and the potential of the carrier holding electrode is determined based on a potential at which electrons are supplied from the carrier holding electrode or a silver / silver chloride electrode potential reference. It is controlled to + 0.3V, and a microorganism group involved in methane fermentation is supported on the carrier and activated.

また、本発明の微生物群担持担体(微生物群が担持された担体の作製方法)の作製方法は、電極表面の少なくとも一部に疎水性の担体を備えた担体保持電極とメタン生成菌群及びメタン生成菌群の基質となる物質を少なくとも含む培養液とを接触させ、担体保持電極の電位を担体保持電極から電子が供給される電位に制御し、担体にメタン生成菌群を担持させて活性化させるようにしている。尚、本発明によれば、メタン生成菌群として、水素資化性メタン菌や酢酸資化性メタン菌を担持させて活性化させ得る。したがって、水素資化性メタン菌を担持させて活性化させる場合には、基質として二酸化炭素と水素を培養液に含ませればよく、酢酸資化性メタン菌を担持させて活性化させる場合には、酢酸等の低級脂肪酸(VFA)を培養液に含ませればよい。 Further, a method for manufacturing a microorganisms supporting carrier of the present invention (a method for manufacturing a carrier microorganisms is carried) is at least partially provided with hydrophobicity of the support carrier holding electrode and the methanogens group and methane electrode surface Contact with a culture solution containing at least a substance that is a substrate for the bacteria group, control the potential of the carrier holding electrode to the potential at which electrons are supplied from the carrier holding electrode, and activate the carrier by supporting the methanogenic bacteria group on the carrier I try to let them. According to the present invention, hydrogen-utilizing methane bacteria and acetic acid-assimilating methane bacteria can be carried and activated as the methanogenic bacteria group. Therefore, when supporting and activating hydrogen-assimilating methane bacteria, carbon dioxide and hydrogen may be included in the culture solution as substrates, and when supporting and activating acetic acid-assimilating methane bacteria In addition, a lower fatty acid (VFA) such as acetic acid may be included in the culture solution.

ここで、本発明の微生物群担持担体の作製方法(微生物群が担持された担体の作製方法)において、担体保持電極を作用電極とし、作用電極と対電極と参照電極とをポテンシオスタットに結線し、メタン発酵液または培養液と電解液とをイオン交換膜を介して接触させ、メタン発酵液または培養液に作用電極と参照電極とを接触させ、電解液に対電極を接触させ、作用電極の電位を3電極方式で制御することが好ましい。また、担体保持電極を作用電極とし、作用電極と対電極と参照電極とをポテンシオスタットに結線し、メタン発酵液または培養液と対電極とをイオン交換膜を介して接触させ、メタン発酵液または培養液に作用電極と参照電極とを接触させ、作用電極の電位を3電極方式で制御することが好ましい。この場合、担体保持電極の電位を、担体保持電極から電子が供給される電位である−0.8V〜−1.0V(銀・塩化銀電極電位基準)に制御することが好ましい。また、担体は炭素繊維であることが好ましい。 Here, in the method for producing a microorganism group-carrying carrier of the present invention (a method for producing a carrier carrying a microorganism group) , the carrier holding electrode is used as a working electrode, and the working electrode, the counter electrode, and the reference electrode are connected to a potentiostat. The methane fermentation broth or culture solution and the electrolytic solution are brought into contact with each other through an ion exchange membrane, the working electrode and the reference electrode are brought into contact with the methane fermentation broth or culture solution, the counter electrode is brought into contact with the electrolytic solution, and the working electrode Is preferably controlled by a three-electrode system. In addition, the carrier holding electrode is used as a working electrode, the working electrode, the counter electrode, and the reference electrode are connected to a potentiostat , and the methane fermentation broth or the culture broth is brought into contact with the counter electrode via an ion exchange membrane. Alternatively, the working electrode and the reference electrode are preferably brought into contact with the culture solution, and the potential of the working electrode is preferably controlled by a three-electrode system. In this case, the potential of the carrier holding electrode is preferably controlled to -0.8 V to -1.0 V (silver / silver chloride electrode potential reference), which is a potential at which electrons are supplied from the carrier holding electrode. The carrier is preferably carbon fiber.

尚、本明細書における「活性化」とは、基本的には担持対象微生物群自体の機能が高められることを意味しているが、これに加えて、担持対象微生物が増殖することにより担体に担持された担持対象微生物群全体としての機能が高められる意味も含まれる場合がある。   “Activation” in the present specification basically means that the function of the microorganism group to be supported itself is enhanced, but in addition to this, the carrier microorganism is propagated to grow the carrier. The meaning of enhancing the function as a whole supported microorganism group to be supported may be included.

発明のメタン発酵方法によれば、優れたメタン発酵処理能を発揮させることができ、しかもその能力は有機性廃棄物等を大量投入した高負荷条件下においても発揮されるものとなり、長期に亘り連続して効率よくメタン発酵処理を行うことが可能となる。 According to the methane fermentation method of the present invention, an excellent methane fermentation treatment ability can be exhibited, and the ability is exhibited even under a high load condition in which a large amount of organic waste or the like is introduced, and for a long time. It becomes possible to perform the methane fermentation treatment continuously and efficiently.

さらに、本発明の微生物群担持担体の作製方法(微生物群が担持された担体の作製方法)によれば、メタン発酵処理において有用な微生物群を担持対象として担体に担持させて活性化させた担体を得ることができる。したがって、この担体をメタン発酵処理に使用することで、優れたメタン発酵処理能を発揮し、その能力は有機性廃棄物等を大量投入した高負荷条件下においても発揮され得るものとなり、長期に亘り連続して効率よくメタン発酵処理を行うことが可能となる。また、メタン生成菌群を担体に担持させて活性化させた微生物群担持担体を作製することで、長期に亘り効率よく連続してメタン生成を行うことが可能となる。 Furthermore, according to the method for producing a carrier for supporting a microorganism group of the present invention (a method for producing a carrier on which a microorganism group is supported) , a carrier activated by supporting a microorganism group useful for methane fermentation treatment on a carrier. Can be obtained. Therefore, this carrier by using methane fermentation treatment, exhibit excellent methane fermentation treatment capacity, its capacity becomes that can be exhibited even at high load conditions large quantities have been introduced organic waste, etc., long-term It is possible to perform the methane fermentation treatment efficiently continuously over a period of. In addition, by producing a microorganism group-supporting carrier in which a methanogenic bacterium group is supported on a carrier and activated, methane can be efficiently and continuously produced over a long period of time.

参考例A−1において使用した実験装置の断面図である。It is sectional drawing of the experimental apparatus used in Reference Example A-1. 参考例A−1におけるメタン発酵槽の運転条件(負荷条件)を示す図である。It is a figure which shows the driving | running condition (load condition) of the methane fermenter in Reference Example A-1. 参考例A−1において得られた設定電位とガス生成速度の関係を示す図である。It is a figure which shows the relationship between the setting electric potential and gas generation rate which were obtained in Reference example A-1. 参考例A−1において得られた設定電位と化学的酸素要求量(COD)除去速度の関係を示す図である。It is a figure which shows the relationship between the setting electric potential obtained in Reference Example A-1, and a chemical oxygen demand (COD) removal rate. 参考例A−1において得られた設定電位と浮遊固形分(SS)除去速度の関係を示す図である。It is a figure which shows the relationship between the setting electric potential obtained in Reference Example A-1, and floating solid content (SS) removal rate. 参考例A−1において得られた設定電位と低級脂肪酸濃度の関係を示す図である。It is a figure which shows the relationship between the setting potential obtained in Reference Example A-1, and a lower fatty acid concentration. 参考例A−2において得られた発酵液画分の全菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of all the microbe of the fermented liquor fraction obtained in Reference Example A-2. 参考例A−2において得られた発酵液画分のメタン生成菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of the methanogen of the fermented liquor fraction obtained in Reference Example A-2. 参考例A−2において得られた担体付着画分の全菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of all the microbes of the carrier adhesion fraction obtained in Reference Example A-2. 参考例A−2において得られた担体付着画分のメタン生成菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of the methanogen of the carrier adhesion fraction obtained in Reference Example A-2. 参考例A−2において、T−RFLPにより細菌群集構造を解析した結果を示す図である。In Reference Example A-2, it is a figure which shows the result of having analyzed the bacterial community structure by T-RFLP. 参考例A−2において、設定電位が−0.6Vの場合の炭素板上の細菌群集構造をTAクローニングにより解析した結果を示す図である。In Reference Example A-2, it is a figure which shows the result of having analyzed the bacterial community structure on the carbon plate in case setting potential is -0.6V by TA cloning. 参考例A−2において、T−RFLPにより古細菌群集構造を解析した結果を示す図である。In Reference Example A-2, it is a figure which shows the result of having analyzed the archaeal community structure by T-RFLP. 参考例A−2において、設定電位が−0.6Vの場合の炭素板上の古細菌群集構造をTAクローニングにより解析した結果を示す図である。In reference example A-2, it is a figure which shows the result of having analyzed the archaea community structure on the carbon plate in case setting potential is -0.6V by TA cloning. 参考例A−3において、メタン生成菌のメタン生成活性の電位依存性を示す図である。In Reference Example A-3, it is a figure which shows the electric potential dependence of the methanogenic activity of a methanogen. 参考例Aー4において、担体の種類等によるガス生成速度の違いについて実験した結果を示す図である。In Reference Example A-4, it is a figure which shows the result of having experimented about the difference in the gas generation rate by the kind etc. of support | carrier. 参考例A−3において使用した実験装置の断面図である。It is sectional drawing of the experimental apparatus used in Reference Example A-3. 参考例B−1におけるメタン発酵槽の運転条件(負荷条件)を示す図である。It is a figure which shows the driving | running condition (load condition) of the methane fermenter in Reference Example B-1. 参考例B−1において得られた設定電位とガス生成速度の関係を示す図である。It is a figure which shows the relationship between the setting electric potential obtained in Reference Example B-1, and a gas production rate. 参考例B−1において得られた設定電位と化学的酸素要求量(COD)除去速度の関係を示す図である。It is a figure which shows the relationship between the setting electric potential obtained in Reference Example B-1, and a chemical oxygen demand (COD) removal rate. 参考例B−1において得られた設定電位と浮遊固形分(SS)除去速度の関係を示す図である。It is a figure which shows the relationship between the setting electric potential obtained in Reference Example B-1, and floating solid content (SS) removal rate. 参考例B−1において得られた設定電位と低級脂肪酸濃度の関係を示す図である。It is a figure which shows the relationship between the setting potential obtained in Reference Example B-1, and a lower fatty acid concentration. 参考例B−2において得られた発酵液画分の全菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of all the microbe of the fermented liquor fraction obtained in Reference Example B-2. 参考例B−2において得られた発酵液画分のメタン生成菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of the methanogen of the fermented liquor fraction obtained in Reference Example B-2. 参考例B−2において得られた担体付着画分の全菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of all the microbes of the carrier adhesion fraction obtained in Reference Example B-2. 参考例B−2において得られた担体付着画分のメタン生成菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of the methanogen of the carrier adhesion fraction obtained in Reference Example B-2. 模擬有機性廃棄物のボルタンメトリー測定を行った結果を示す図である。It is a figure which shows the result of having performed the voltammetric measurement of the simulated organic waste. 参考例B−2において、T−RFLPにより細菌群集構造を解析した結果を示す図である。In Reference Example B-2, it is a figure which shows the result of having analyzed the bacterial community structure by T-RFLP. 参考例B−2において、T−RFLPにより古細菌群集構造を解析した結果を示す図である。In Reference Example B-2, it is a figure which shows the result of having analyzed the archaeal community structure by T-RFLP. 第一の実施形態Aにかかる処理装置の一例を示す断面図である。It is sectional drawing which shows an example of the processing apparatus concerning 1st Embodiment A. 第一の実施形態Bにかかる処理装置の一例を示す断面図である。It is sectional drawing which shows an example of the processing apparatus concerning 1st Embodiment B. 第一の実施形態Cにかかる処理装置の一例を示す断面図である。It is sectional drawing which shows an example of the processing apparatus concerning 1st Embodiment C. 第一の実施形態Dにかかる処理装置の一例を示す断面図である。It is sectional drawing which shows an example of the processing apparatus concerning 1st Embodiment D. 第二の実施形態にかかる処理装置の一例を示す断面図である。It is sectional drawing which shows an example of the processing apparatus concerning 2nd embodiment. 処理装置の他の形態の一例を示す断面図である。It is sectional drawing which shows an example of the other form of a processing apparatus. 実施例1におけるメタン発酵槽の運転条件(負荷条件)を示す図である。It is a figure which shows the driving | running condition (load condition) of the methane fermenter in Example 1. FIG. 実施例1におけるガス生成速度の経時変化を示す図である。It is a figure which shows the time-dependent change of the gas production | generation speed | rate in Example 1. FIG. 実施例1におけるバイオガス中のメタンガス含有率の経時変化を示す図である。It is a figure which shows the time-dependent change of the methane gas content rate in the biogas in Example 1. FIG. 実施例1におけるメタン発酵液のVFA濃度の経時変化を示す図である。It is a figure which shows the time-dependent change of the VFA density | concentration of the methane fermentation liquid in Example 1. FIG. 実施例1における有機物負荷量に対するCOD除去率を示す図である。It is a figure which shows the COD removal rate with respect to the organic substance load in Example 1. FIG. 実施例1における有機物負荷量に対するSS除去率を示す図である。It is a figure which shows SS removal rate with respect to the organic substance load in Example 1. FIG. 実施例2において得られた発酵液画分の全菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of all the microbe of the fermentation liquid fraction obtained in Example 2. FIG. 実施例2において得られた担体付着画分の全菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of all the microbes of the carrier adhesion fraction obtained in Example 2. FIG. 実施例2において得られた発酵液画分のメタン菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of the methane microbe of the fermented liquor fraction obtained in Example 2. 実施例2において得られた担体付着画分のメタン菌の定量PCR結果を示す図である。It is a figure which shows the quantitative PCR result of the methane microbe of the carrier adhesion fraction obtained in Example 2. 実施例2において、T−RFLPにより古細菌群集構造を解析した結果を示す図である。In Example 2, it is a figure which shows the result of having analyzed the archaeal community structure by T-RFLP.

以下、本発明を実施するための形態について、図面に基づいて詳細に説明する。   Hereinafter, embodiments for carrying out the present invention will be described in detail with reference to the drawings.

本発明の生物学的処理方法は、電極表面の少なくとも一部に微生物を担持し得る担体を備えた担体保持電極と担体への担持対象微生物群を少なくとも含む微生物群集と培養液とを接触させ、担体保持電極の電位を担持対象微生物群の至適範囲に制御しながら生物学的処理を行うようにしている。また、本発明の生物学的処理方法を実施することで、担体に担持対象微生物群を担持させて活性化させることができる。   In the biological treatment method of the present invention, a carrier holding electrode provided with a carrier capable of supporting microorganisms on at least a part of the electrode surface, a microbial community including at least a microorganism group to be supported on the carrier, and a culture solution are contacted, Biological treatment is performed while controlling the potential of the carrier holding electrode within the optimum range of the microorganism group to be supported. Moreover, by carrying out the biological treatment method of the present invention, it is possible to activate a carrier group to be supported on a carrier.

また、本発明の物質処理方法は、電極表面の少なくとも一部に微生物を担持し得る担体を備えた担体保持電極と担持対象微生物群として物質変換処理能を有する微生物群を少なくとも含む微生物群集と担持対象微生物群により変換処理される被処理物を含む培養液とを接触させ、担体保持電極の電位を担持対象微生物群の至適範囲に制御しながら被処理物を変換処理するようにしている。また、本発明の物質生産方法は、電極表面の少なくとも一部に微生物を担持し得る担体を備えた担体保持電極と担持対象微生物群として物質生産処理能を有する微生物群を少なくとも含む微生物群集と担持対象微生物群による生産物の生成源物質を含む培養液とを接触させ、担体保持電極の電位を担持対象微生物群の至適範囲に制御しながら物質生産するようにしている。そして、本発明の物質処理方法を実施することで、担体に物質変換処理能を有する微生物群を担持させて活性化させることができる。また、本発明の物質生産方法を実施することで、担体に物質生産処理能を有する微生物群を担持させて活性化させることができる。   In addition, the material treatment method of the present invention comprises a carrier holding electrode provided with a carrier capable of supporting microorganisms on at least a part of the electrode surface, and a microbial community including at least a microorganism group having a substance conversion treatment ability as a supporting target microorganism group. A culture solution containing an object to be processed that is converted by the target microorganism group is brought into contact, and the object to be processed is converted while controlling the potential of the carrier holding electrode within the optimum range of the target microorganism group. Further, the substance production method of the present invention includes a carrier holding electrode provided with a carrier capable of supporting microorganisms on at least a part of the electrode surface, and a microorganism community including at least a microorganism group having substance production processing ability as a supporting target microorganism group. A substance is produced while contacting the culture solution containing the production source material of the product of the target microorganism group and controlling the potential of the carrier holding electrode within the optimum range of the target microorganism group. And by implementing the substance processing method of this invention, the microorganism group which has substance conversion processing ability can be carry | supported and activated on a support | carrier. Moreover, by carrying out the substance production method of the present invention, it is possible to activate a carrier by supporting a group of microorganisms having substance production processing ability.

本発明では、被処理物に対し、分解、酸化、還元などの変換処理を行うことのできる微生物群全般、あるいはある生成源物質を利用して物質を生産する能力を有する微生物群全般を担持対象微生物群とすることができる。   In the present invention, the entire microorganism group that can perform conversion treatment such as decomposition, oxidation, reduction, etc. on the object to be processed or the entire microorganism group that has the ability to produce a substance using a certain source material is supported. It can be a microorganism group.

例えば、SS(固形浮遊物)の分解、COD(化学的酸素要求量)の分解除去、TOC(全有機炭素)の分解除去、テトラクロロエチレン(PCE)、ジクロロエチレン(DCE)及びビニルクロライド(VC)の脱塩素化処理等を行う機能を有する公知あるいは新規の微生物を担持対象微生物群とすることができる。例えば、SS(固形浮遊物)の分解、COD(化学的酸素要求量)の分解除去、TOC(全有機炭素)の分解除去には、メタン発酵槽から取得される汚泥に含まれる微生物群を使用することができる。また、テトラクロロエチレン(PCE)の脱塩素化には例えばDesulfitobacterium, Dehalococcoides, Dehalobacter, Geobacter等、ジクロロエチレン(DCE)及びビニルクロライド(VC)の脱塩素化には例えばDehalococcoides等の微生物群を使用することができる。   For example, decomposition of SS (solid suspended matter), decomposition removal of COD (chemical oxygen demand), decomposition removal of TOC (total organic carbon), removal of tetrachlorethylene (PCE), dichloroethylene (DCE) and vinyl chloride (VC) A known or new microorganism having a function of performing a chlorination treatment or the like can be used as a supported microorganism group. For example, microorganisms contained in sludge obtained from methane fermenters are used for SS (solid suspended solids) decomposition, COD (chemical oxygen demand) decomposition removal, and TOC (total organic carbon) decomposition removal. can do. Further, for the dechlorination of tetrachlorethylene (PCE), for example, Desulfitobacterium, Dehalococcoides, Dehalobacter, Geobacter and the like, and for the dechlorination of dichloroethylene (DCE) and vinyl chloride (VC), a microorganism group such as Dehalococcoides can be used. .

また、例えば、メタンガス、水素、アミノ酸、各種有機物を生産する機能を有する公知あるいは新規の微生物を担持対象微生物群とすることができる。例えば、水素と二酸化炭素を生成源としてメタンガスを生成する水素資化性メタン生成菌(例えば、Methanothermobacter thermautotrophicus等)、酢酸を生成源としてメタンガスを生成する酢酸資化性メタン生成菌(例えば、Methanosarcina thermophila)、グルコースからエタノールやブタノール、アセトンを生産するClostridium acetobutylicum等が挙げられるが、これらに限定されるものではない。   Further, for example, known or novel microorganisms having a function of producing methane gas, hydrogen, amino acids, and various organic substances can be used as the supported microorganism group. For example, hydrogen-utilizing methanogens that produce methane gas using hydrogen and carbon dioxide as sources (for example, Methanothermobacter thermautotrophicus), acetic acid-assimilating methanogens that produce methane gas using acetic acid as a source (for example, Methanosarcina thermophila ), Clostridium acetobutylicum that produces ethanol, butanol, and acetone from glucose, but is not limited thereto.

本発明において用いられる担体保持電極は、微生物反応プロセスに合わせて、電極表面に保持される担体の性質を適宜選択して用いることができる。例えば、親水性の担体に付着し得る微生物を担持させる場合には、親水性の担体を用いればよいし、疎水性の担体に付着し得る微生物を担持させる場合には、疎水性の担体を用いればよい。つまり、電極の性質に依存することなく、担体の性質を適宜選択して微生物反応プロセスに合わせて微生物群を担持させることができる。したがって、例えば、電極の表面に親水性の担体と疎水性の担体の双方を保持させることで、親水性の担体に付着する微生物と疎水性の担体に付着する微生物の双方を担持させることも容易に行うことができる。また、担体は、繊維状や多孔質体、粒状物等の三次元構造として表面積を増大させ、微生物の担持量を増大することのできる形態とすることが好ましい。   The carrier holding electrode used in the present invention can be used by appropriately selecting the nature of the carrier held on the electrode surface in accordance with the microbial reaction process. For example, when a microorganism that can adhere to a hydrophilic carrier is supported, a hydrophilic carrier may be used. When a microorganism that can adhere to a hydrophobic carrier is supported, a hydrophobic carrier may be used. That's fine. That is, the microorganism group can be supported in accordance with the microorganism reaction process by appropriately selecting the nature of the carrier without depending on the nature of the electrode. Therefore, for example, by holding both the hydrophilic carrier and the hydrophobic carrier on the surface of the electrode, it is easy to carry both the microorganisms attached to the hydrophilic carrier and the microorganisms attached to the hydrophobic carrier. Can be done. Moreover, it is preferable that a support | carrier is made into the form which can increase a surface area as a three-dimensional structure, such as a fibrous form, a porous body, and a granular material, and can increase the load of microorganisms.

ここで、メタン発酵処理またはメタンガス生成を実施する場合には、疎水性担体を用いることが好ましい。疎水性担体としては、例えば、炭素繊維を用いることが好適であり、空隙率が25%〜98%の炭素繊維、好適には空隙率が50〜98%の炭素繊維、より好適には空隙率が98%の炭素繊維を使用することができるが、疎水性担体は炭素繊維に限定されるものではなく、例えば、ポリエチレン製やポリプロピレン製の繊維等の担体を用いてもよい。尚、炭素繊維は、高い空隙率の確保が容易であり、例えば炭素繊維不織布は、高い空隙率(98%)を確保し易く、しかも安価に入手でき、好適である。   Here, when carrying out methane fermentation treatment or methane gas generation, it is preferable to use a hydrophobic carrier. As the hydrophobic carrier, for example, carbon fibers are preferably used, carbon fibers having a porosity of 25% to 98%, preferably carbon fibers having a porosity of 50 to 98%, and more preferably a porosity. 98% carbon fiber can be used, but the hydrophobic carrier is not limited to carbon fiber, and for example, a carrier such as a fiber made of polyethylene or polypropylene may be used. Carbon fiber is easy to secure a high porosity, and for example, a carbon fiber nonwoven fabric is suitable because it is easy to ensure a high porosity (98%) and can be obtained at low cost.

担体保持電極に用いられる電極については、その材質は特に限定されるものではなく、電極上で還元反応が生じ得るあらゆる電極を使用することができる。例えば、炭素電極が好適であるが、これに限定されるものではない。   The material used for the carrier holding electrode is not particularly limited, and any electrode capable of causing a reduction reaction on the electrode can be used. For example, although a carbon electrode is suitable, it is not limited to this.

尚、本発明において用いられる担体保持電極は、電極表面の少なくとも一部に担体が備えられていれば良いが、電極表面の片面に備えられていることが好適であり、電極表面の全体に備えられていることが最も好適である。電極表面における担体保持面積を高めれば高める程、微生物を担持させやすくなる。担体を電極表面に備える方法としては、接着剤による接着や、担体を袋状や筒状にして電極に被せて覆う方法などが挙げられるがこれらに限定されるものではない。   The carrier holding electrode used in the present invention may be provided with a carrier on at least a part of the electrode surface, but is preferably provided on one side of the electrode surface and provided on the entire electrode surface. Most preferably. The higher the carrier holding area on the electrode surface, the easier it is to support microorganisms. Examples of the method of providing the carrier on the electrode surface include adhesion by an adhesive, and a method of covering the electrode by covering the electrode with a bag or cylinder, but is not limited thereto.

ここで、微生物を担持し得る担体は、電極とメタン発酵液との接触を確保し得る通液性を有するものとすることが好ましい。この場合、担体の電極近傍まで十分に微生物を担持させることができると共に、電極近傍の電位の制御性を確保して、担体上の微生物を十分に活性化させることができる。つまり、仮に担体の素材を炭素のような導電性の素材とした場合においても、微生物の担持量を高める上で空隙率等を向上させれば、導電性能は大幅に低下して実質的には電流が流れなくなるが、担体を電極とメタン発酵液との接触を確保し得る通液性を有するものとしておけば、担体の空隙を満たすメタン発酵液の電位が制御されて担体の電位環境を微生物にとって至適な範囲に制御することができる。   Here, it is preferable that the carrier capable of supporting the microorganism has liquid permeability capable of ensuring contact between the electrode and the methane fermentation broth. In this case, the microorganisms can be sufficiently loaded up to the vicinity of the electrode of the carrier, and the controllability of the potential in the vicinity of the electrode can be ensured to sufficiently activate the microorganism on the carrier. In other words, even if the carrier material is a conductive material such as carbon, if the porosity is increased in order to increase the amount of microorganisms supported, the conductivity performance will be substantially reduced and substantially reduced. If the carrier does not flow, but the carrier has liquid permeability that can ensure contact between the electrode and the methane fermentation broth, the potential of the methane fermentation broth that fills the gap in the carrier is controlled, and the potential environment of the carrier is reduced to microorganisms. Can be controlled within the optimum range.

培養液は、微生物の培養の際に使用される通常の培養液を用いればよく、微生物のエネルギー源となる物質や、pH等の培養環境を制御するための物質等を適宜添加して使用すればよい。尚、培養液には通常、水素イオン、ナトリウムイオン(Na)、カリウムイオン(K)などの一価の陽イオンが含まれていることから、培養液自体に通電性があり、担体保持電極自体の電位制御は容易に行うことができる。 As the culture solution, a normal culture solution used for culturing microorganisms may be used, and a substance that serves as an energy source for microorganisms, a substance for controlling the culture environment such as pH, and the like may be appropriately added. That's fine. The culture solution usually contains monovalent cations such as hydrogen ions, sodium ions (Na + ), and potassium ions (K + ), so that the culture solution itself has electrical conductivity and supports the carrier. The potential control of the electrode itself can be easily performed.

尚、担体保持電極と担持対象微生物群と培養液との接触方法は特に限定されるものではない。例えば、培養液に担体保持電極と担持対象微生物群とを別々に入れるようにしてもよいし、担持対象微生物群あるいは担持対象微生物群を含む微生物群集を例えばバイオフィルムのような形態で担体に予め担持させておき、これを培養液に入れるようにしてもよい。いずれの場合にも、担体保持電極の担体に担持対象微生物群を担持させて活性化させることができる。本発明によれば、担持対象微生物群を担持させて活性化させることができるのは勿論のこと、担持対象微生物群を含む微生物群集のうち、担持対象微生物群を主要な構成成分として担持させて活性化させることができる。つまり、複数種の微生物群を含む微生物群集から所望の微生物群を主要な構成成分として担体に担持させて活性化させることができる。   The contact method between the carrier holding electrode, the target microorganism group and the culture solution is not particularly limited. For example, the carrier holding electrode and the microorganism group to be supported may be separately added to the culture solution, or the microorganism group including the microorganism group to be supported or the microorganism group to be supported is previously loaded on the carrier in the form of a biofilm, for example. You may make it carry | support and make this put into a culture solution. In any case, the target microorganism group can be supported by the carrier of the carrier holding electrode and activated. According to the present invention, it is possible to carry and activate a supported target microorganism group, and of the microorganism group including the supported target microorganism group, the supported target microorganism group is supported as a main component. Can be activated. That is, it is possible to activate a desired microorganism group as a main constituent from a microorganism group including a plurality of types of microorganism groups.

担持対象微生物群の至適範囲は、以下に説明する実験方法により導かれる。即ち、被処理物を変換処理する能力を有する微生物群を担持対象とする場合、一定量の被処理物を培養液に添加し、この培養液に担体保持電極と担持対象微生物群を少なくとも含む微生物群集とを接触させて、担体保持電極を各種電位に一定期間制御し、培養液に含まれる被処理物の量が大幅に低減している電位範囲を至適範囲とすることができる。また、生産物を生産する微生物群を担持対象とする場合、一定量の生成源物質を培養液に添加し、この培養液に担体保持電極と担持対象微生物群を少なくとも含む微生物群集とを接触させて、担体保持電極を各種電位に一定期間制御し、生産物の生成量が多い電位範囲を至適範囲とすることができる。   The optimum range of the microorganism group to be supported is derived by the experimental method described below. That is, when a microorganism group having an ability to convert the object to be treated is to be supported, a certain amount of the object to be treated is added to the culture solution, and the microorganism includes at least the carrier holding electrode and the object microorganism group to be supported in the culture solution. By contacting the crowd and controlling the carrier holding electrode at various potentials for a certain period of time, the potential range in which the amount of the object to be treated contained in the culture solution is greatly reduced can be made the optimum range. When a microorganism group that produces a product is to be supported, a certain amount of a source material is added to the culture solution, and the culture solution is brought into contact with a carrier holding electrode and a microorganism community that includes at least the supported microorganism group. Thus, the carrier holding electrode can be controlled to various potentials for a certain period of time, and the potential range where the amount of product produced is large can be made the optimum range.

本発明によれば、担体保持電極の担体に担持対象微生物群を担持させて活性化することができる。したがって、高負荷条件下で微生物を利用した物質処理方法や物質生産方法を実施しても、優れた処理能力を発揮させて効率よく実施することができる。また、本発明によれば、目的の処理を阻害する微生物群を失活させたり、あるいは除去することで、目的の処理を効率よく実施することも可能となる場合もある。尚、本発明の生物学的処理方法において、高負荷条件下で実施しても、優れた処理能力を発揮させて効率よく実施することができる要因の一つとして、例えば以下のことが考えられる。即ち、本発明の生物学的処理方法により、担体に担持対象微生物群を担持させて活性化させながらも、培養液中の全菌に占める担持対象微生物群の割合を増加させることができ、担体保持電極を培養液とを含めた処理槽全体としての処理能力が向上していることが要因の一つとして考えられる。いずれにしても、本発明の構成をとることによって、優れた処理能力を発揮させることができる。 According to the present invention, the target microorganism group can be supported by the carrier of the carrier holding electrode and activated. Therefore, even if a material processing method or a material production method using microorganisms is performed under high load conditions, it can be efficiently performed with its excellent processing capacity. Moreover, according to the present invention, it may be possible to efficiently carry out the target treatment by inactivating or removing the microorganism group that inhibits the target treatment. In addition, in the biological treatment method of the present invention, even if carried out under high load conditions, for example, the following can be considered as one of the factors that can be carried out efficiently while exhibiting excellent treatment capacity. . That is, according to the biological treatment method of the present invention, while the carrier target microorganism group is supported on the carrier and activated, the proportion of the target microorganism group in the total bacteria in the culture solution can be increased, and the carrier One of the factors can be considered that the processing capacity of the entire processing tank including the holding electrode and the culture solution is improved. In any case, by taking the configuration of the present invention, it is possible to exhibit excellent processing capability.

以下、本発明の生物学的処理方法としてメタン発酵処理を実施した場合について具体的に説明する。   Hereinafter, the case where a methane fermentation process is implemented as a biological treatment method of the present invention will be specifically described.

メタン発酵処理は、有機性廃棄物をメタン発酵して減容化し、その過程でメタンガスを含むバイオガスを生成させて回収するものである。   In the methane fermentation process, organic waste is reduced in volume by methane fermentation, and biogas containing methane gas is generated and recovered in the process.

メタン発酵液には、有機性廃棄物等のメタン発酵処理が行われているメタン発酵槽のメタン発酵液やメタン発酵汚泥を添加した培養液を用いることができる。また、メタン発酵を行うための微生物群を人工的に培養した微生物群集を添加した培養液を用いることもできる。   As the methane fermentation liquid, a methane fermentation liquid in a methane fermentation tank in which methane fermentation treatment such as organic waste is performed or a culture liquid to which methane fermentation sludge is added can be used. Moreover, the culture solution which added the microorganism community which cultured the microorganism group for performing methane fermentation artificially can also be used.

メタン発酵液には、有機性基質として有機性廃棄物が投入される。有機性廃棄物としては、畜産廃棄物、生ゴミ、廃水処理汚泥、稲藁や麦藁等の藁類、紙ごみ、各種バイオマス等などが挙げられるが、これらに限定されるものではない。また、有機性廃棄物は、その性状により、必要に応じて、破砕や分別などの前処理を行ってからメタン発酵処理に供される。   Organic waste is introduced into the methane fermentation broth as an organic substrate. Examples of the organic waste include, but are not limited to, livestock waste, raw garbage, wastewater treatment sludge, rice cakes such as rice straw and wheat straw, paper waste, various biomass, and the like. In addition, the organic waste is subjected to a methane fermentation treatment after performing pretreatment such as crushing and fractionation, if necessary, depending on its properties.

担体保持電極としては、上記の通り、電極、例えば炭素板の表面の少なくとも一部に疎水性の担体、例えば炭素繊維が備えられたものがメタン発酵液に浸される。   As described above, as the carrier holding electrode, an electrode such as one having a hydrophobic carrier such as carbon fiber provided on at least a part of the surface of the carbon plate is immersed in the methane fermentation broth.

担体保持電極の電位は、担体保持電極にて還元反応が生じ得る電位または銀・塩化銀電極電位基準で+0.3Vに制御する。尚、担体保持電極にて還元反応が生じ得る電位は、メタン発酵液が一般的に銀・塩化銀電極電位基準で−0.5V程度であることから、−0.6Vを含んで−0.6Vよりもマイナス側に大きくすれば、担体保持電極にて還元反応は生じ得るが、マイナス側に大きくし過ぎると水の電気分解が激しく生じてメタン発酵が停止する虞があると共に、メタン発酵から水素発酵への移行が生じる虞もあるので、それよりも小さな電位とすることが好適である。具体的には−1.0Vを含んで−1.0Vよりもマイナス側に大きくすると、メタン発酵から水素発酵への移行が生じる可能性があるので、−1.0Vよりも絶対値基準で小さくすることが好適である。因みに、−1.2V程度であれば水の電気分解が激しく生じることはない。尚、後述するイオン交換膜を備えた形態の場合には、−1.0Vよりもマイナス側に大きくしても水素発酵への移行は生じないので、−1.0Vよりもマイナス側に大きくしてもよい。このように担体保持電極の電位を制御することにより、メタン発酵処理に関与する微生物群が担体保持電極の担体に担持されて活性化し、メタン発酵処理の一連の微生物反応である、SS分解処理、COD分解除去処理、低級脂肪酸分解処理及びメタン生成が効率よく進行する。また、本願発明者等の実験によれば、有機物負荷量を徐々に増加させながら電位を上記値に44日間制御し続けることで、最終的に有機物負荷量を27.8gCOD/l/日としても、メタン生成が問題なく進行することが確認され、特に、設定電位を−1.0Vとした場合については、有機物負荷量を徐々に増加させながら電位を54日間制御し続けることで、最終的に有機物負荷量を32.7gCOD/l/日としてメタン発酵を行っても、メタン生成が問題なく進行することが確認された。このことから、設定電位を銀・塩化銀電極電位基準で−0.8V〜−1.0Vまたは+0.3V、好適には−1.0Vに制御して、例えば最終的な有機物負荷量が20gCOD/l/日となるように有機物負荷量を徐々に増加させて少なくとも44日間馴養を行うことで、少なくとも有機物負荷量27.8gCOD/l/日という極めて高負荷な運転条件下においてもメタン発酵処理を進行させることができる微生物群担持担体を作製することができる。   The potential of the carrier holding electrode is controlled to +0.3 V based on the potential at which a reduction reaction can occur at the carrier holding electrode or the silver / silver chloride electrode potential reference. The potential at which the reduction reaction can occur at the support holding electrode is generally about -0.5 V on the basis of the silver / silver chloride electrode potential for methane fermentation liquor. If it is made larger than 6V to the minus side, a reduction reaction may occur at the carrier holding electrode, but if it is made too large on the minus side, water electrolysis may occur vigorously and methane fermentation may be stopped. Since there is a possibility that a shift to hydrogen fermentation may occur, it is preferable to set a smaller potential. Specifically, if -1.0V is included and it is made larger than -1.0V to the minus side, there is a possibility that the transition from methane fermentation to hydrogen fermentation may occur, so it is smaller than -1.0V on an absolute value basis. It is preferable to do. Incidentally, if it is about -1.2V, electrolysis of water does not occur vigorously. In the case of an embodiment provided with an ion exchange membrane, which will be described later, even if it is increased to the minus side from -1.0 V, the shift to hydrogen fermentation does not occur. May be. By controlling the potential of the carrier holding electrode in this way, the microbial group involved in the methane fermentation treatment is activated by being carried on the carrier of the carrier holding electrode, and the SS decomposition treatment, which is a series of microbial reactions of the methane fermentation treatment, COD decomposition and removal treatment, lower fatty acid decomposition treatment and methane production proceed efficiently. In addition, according to the experiments by the inventors of the present application, the organic load is finally increased to 27.8 gCOD / l / day by continuously controlling the potential to the above value for 44 days while gradually increasing the load of organic matter. It was confirmed that the methane generation proceeded without any problem. Particularly, in the case where the set potential was set to -1.0 V, the potential was finally controlled by continuously controlling the potential for 54 days while gradually increasing the organic load. Even when methane fermentation was carried out at an organic load of 32.7 g COD / l / day, it was confirmed that methane production proceeded without problems. From this, the set potential is controlled to -0.8 V to -1.0 V or +0.3 V, preferably -1.0 V on the basis of the silver / silver chloride electrode potential, and the final organic load, for example, is 20 gCOD. By gradually increasing the organic load so that it becomes / l / day and acclimatizing for at least 44 days, the methane fermentation treatment is performed even under extremely high load operating conditions of at least 27.8 g COD / l / day. Can be produced.

ここで、本発明のメタン発酵方法は、例えば図30〜図34に示す装置により実施される。以下、第一の実施形態にかかるメタン発酵方法を図30〜図33に基づいて説明し、第二の実施形態にかかるメタン発酵方法を図34に基づいて説明する。   Here, the methane fermentation method of the present invention is implemented by, for example, the apparatus shown in FIGS. Hereinafter, the methane fermentation method according to the first embodiment will be described based on FIGS. 30 to 33, and the methane fermentation method according to the second embodiment will be described based on FIG. 34.

<第一の実施形態>
第一の実施形態にかかるメタン発酵方法は、電極表面の少なくとも一部に微生物を担持し得る疎水性の担体を備えた担体保持電極を作用電極とし、作用電極と対電極と参照電極とを定電位設定装置に結線し、メタン発酵液と電解液とをイオン交換膜を介して接触させ、メタン発酵液と作用電極と参照電極とを接触させ、電解液に対電極を接触させ、作用電極の電位を3電極方式で制御するようにしている。
<First embodiment>
In the methane fermentation method according to the first embodiment, the working electrode, the counter electrode, and the reference electrode are defined by using a carrier holding electrode having a hydrophobic carrier capable of carrying microorganisms on at least a part of the electrode surface. Connect to the potential setting device, contact the methane fermentation broth and electrolyte through the ion exchange membrane, contact the methane fermentation broth, working electrode, and reference electrode, contact the counter electrode to the electrolyte, The potential is controlled by a three-electrode system.

第一の実施形態にかかるメタン発酵方法は、例えば図30〜図33に示す装置1により実施される。即ち、図30〜図33に示す処理装置1は、イオン交換膜6によって仕切られた二つの槽のうちの一方の槽を処理槽7とし、他方の槽を対電極槽8とし、処理槽7にはメタン発酵液4が収容されると共に作用電極9と参照電極11が浸され、対電極槽8には電解液4aが収容されると共に対電極10が浸され、作用電極9と対電極10は定電位設定装置12に結線され、作用電極9の電位を3電極方式で制御するようにしている。   The methane fermentation method according to the first embodiment is performed by, for example, the apparatus 1 shown in FIGS. That is, in the processing apparatus 1 shown in FIGS. 30 to 33, one of the two tanks partitioned by the ion exchange membrane 6 is used as the processing tank 7, and the other tank is used as the counter electrode tank 8. The methane fermentation liquid 4 is accommodated in the working electrode 9 and the reference electrode 11, and the counter electrode tank 8 is filled with the electrolytic solution 4a and the counter electrode 10 is immersed in the working electrode 9 and the counter electrode 10. Is connected to the constant potential setting device 12, and the potential of the working electrode 9 is controlled by a three-electrode system.

このように、3電極方式で作用電極9の電位を制御することで、作用電極9の電位を厳密に設定電位に制御することができる。詳細には、定電位設定装置(ポテンシオスタット)12により、作用電極9と参照電極11との間の電位差を測定し、この電位差が設定電位に達するように作用電極9と対電極10との間に電流を流し、基準となる参照電極11には一切電流が流れないようにしている。尚、3電極方式による電位制御については、例えば、電気化学測定法(上)、技報動出版株式会社、第1版15刷、2004年6月発行の6〜9ページにその詳細が記載されている。   In this way, by controlling the potential of the working electrode 9 by the three-electrode method, the potential of the working electrode 9 can be strictly controlled to the set potential. Specifically, a potential difference between the working electrode 9 and the reference electrode 11 is measured by a constant potential setting device (potentiostat) 12, and the working electrode 9 and the counter electrode 10 are adjusted so that the potential difference reaches the set potential. A current is passed between them so that no current flows through the reference electrode 11 serving as a reference. The details of the potential control by the three-electrode method are described in, for example, pages 6 to 9 of Electrochemical Measurement Method (above), Technical Bulletin Publishing Co., Ltd., 1st edition 15 printing, published in June 2004. ing.

但し、作用電極9と対電極10の極間電圧のみで作用電極9の電位を制御できる場合には、3電極方式とせずともよい。また、図30〜図33では、作用電極9の片面にのみ微生物を担持し得る担体9aを備えるようにしているが、片面の一部に備えるようにしてもよいし、両面に備えるようにしても勿論良い。   However, when the potential of the working electrode 9 can be controlled only by the voltage between the working electrode 9 and the counter electrode 10, the three-electrode system may not be used. 30 to 33, the carrier 9a capable of supporting microorganisms is provided only on one side of the working electrode 9, but it may be provided on a part of one side or on both sides. Is of course good.

また、図30〜図33に示す処理装置1では、処理槽7内のメタン発酵液4の液面よりも上部の空間(ヘッドスペース)に滞留するメタンガスを含むバイオガスを処理槽7の外(処理装置1の外)へ導くガス排出管15aを備え、このガス排出管15aをバルブ15bにより開閉可能としたガス回収手段15により、処理槽7内のバイオガスを回収するようにしている。但し、バイオガスの回収方法は、この方法に限定されない。例えば、ガス回収手段15を備えることなく、処理槽7の上部に開口部を設けて合成ゴム等(例えばシリコーンゴム)の弾性材料でこの開口部を塞ぎ、開口部を塞ぐ弾性材料に注射器の注射針を刺してヘッドスペースからバイオガスを回収するようにしてもよい。合成ゴム等の弾性材料は、注射針を引き抜くと孔が塞がる。したがって、バイオガスの回収を行わないときには、注射針を引き抜いておいても、処理槽7からバイオガスが漏れ出すことがない。   Moreover, in the processing apparatus 1 shown in FIGS. 30-33, the biogas containing the methane gas which retains in the space (head space) above the liquid level of the methane fermentation liquid 4 in the processing tank 7 is outside the processing tank 7 ( A gas exhaust pipe 15a leading to the outside of the processing apparatus 1 is provided, and the biogas in the processing tank 7 is recovered by a gas recovery means 15 that can be opened and closed by a valve 15b. However, the biogas recovery method is not limited to this method. For example, without providing the gas recovery means 15, an opening is provided in the upper part of the processing tank 7, and the opening is closed with an elastic material such as synthetic rubber (for example, silicone rubber), and the syringe is injected into the elastic material that closes the opening. You may make it collect | recover biogas from a head space with a needle. The elastic material such as synthetic rubber closes the hole when the injection needle is pulled out. Therefore, when the biogas is not collected, the biogas does not leak from the processing tank 7 even if the injection needle is pulled out.

さらに、図30〜図33に示す処理装置1では、処理槽7内のメタン発酵液4の液面よりも下部に、処理槽7内のメタン発酵液4を処理槽7の外に導くメタン発酵液排出管16aを備え、このメタン発酵液排出管16aをバルブ16bにより開閉可能としたメタン発酵液採取手段16により、処理槽7内からメタン発酵液4を採取するようにしている。但し、メタン発酵液4の採取方法は、この方法に限定されるものではない。例えば、メタン発酵液採取手段16を備えることなく、処理槽7に開口部を設けて合成ゴム等の弾性材料で塞ぎ、注射器の注射針を刺してメタン発酵液4を採取するようにしてもよい。または両端が開口された管の一端の注射器に接続し、他端をメタン発酵液4に浸けて、管を介してメタン発酵液4を採取するようにしてもよい。これらの場合にも、処理槽7からバイオガスが漏れ出すことはない。   Furthermore, in the processing apparatus 1 shown in FIGS. 30 to 33, methane fermentation for guiding the methane fermentation solution 4 in the treatment tank 7 to the outside of the treatment tank 7 below the liquid level of the methane fermentation solution 4 in the treatment tank 7. A methane fermentation broth 4 is collected from the treatment tank 7 by a methane fermentation broth collecting means 16 that includes a liquid discharge pipe 16a and that can be opened and closed by a valve 16b. However, the method for collecting the methane fermentation broth 4 is not limited to this method. For example, without providing the methane fermentation broth collecting means 16, the processing tank 7 may be provided with an opening and closed with an elastic material such as synthetic rubber, and the injection needle of a syringe may be inserted to collect the methane fermentation broth 4. . Or you may make it connect to the syringe of one end of the pipe | tube with which both ends were opened, immerse the other end in the methane fermentation liquid 4, and extract | collect the methane fermentation liquid 4 through a pipe | tube. Also in these cases, the biogas does not leak from the treatment tank 7.

また、ガス回収手段15やメタン発酵液採取手段16とは別に、メタン発酵液4に物質を添加・供給する手段を設けるようにしてもよい。具体的には、処理槽7の外部からメタン発酵液4に物質を添加・供給することのできる開閉可能な物質導入管を備えるようにしてもよい。この場合には、メタン発酵液に栄養源、中和剤、メタン発酵汚泥等の物質を必要に応じて添加することができる。勿論、有機性基質をこの導入管から供給することもできる。また、環境を嫌気性に維持するためにガスを供給することもできる。但し、メタン発酵液4に物質を添加・供給する手段は必ずしも備える必要はなく、ガス回収手段15やメタン発酵液採取手段16をメタン発酵液4に物質を添加・供給する手段として併用するようにしてもよい。また、上記のように注射器の注射針を弾性材料に差し込んでメタン発酵液4に物質を添加・供給するようにしてもよい。   In addition to the gas recovery means 15 and the methane fermentation broth collecting means 16, a means for adding and supplying substances to the methane fermentation broth 4 may be provided. Specifically, an openable / closable substance introduction pipe that can add and supply substances to the methane fermentation broth 4 from the outside of the treatment tank 7 may be provided. In this case, substances such as nutrient sources, neutralizing agents, and methane fermentation sludge can be added to the methane fermentation broth as necessary. Of course, the organic substrate can also be supplied from this introduction tube. Gas can also be supplied to keep the environment anaerobic. However, it is not always necessary to provide means for adding and supplying substances to the methane fermentation broth 4, and the gas recovery means 15 and the methane fermentation liquid collecting means 16 may be used together as means for adding and supplying substances to the methane fermentation broth 4. May be. Further, as described above, the injection needle of the syringe may be inserted into the elastic material to add and supply the substance to the methane fermentation solution 4.

以下、図30に示す処理装置を用いた場合を第一の実施形態Aとして説明し、図31に示す処理装置を用いた場合を第一の実施形態Bとして説明し、図32に示す処理装置を用いた場合を第一の実施形態Cとして説明し、図33に示す処理装置を用いた場合を第一の実施形態Dとして説明する。   Hereinafter, the case where the processing apparatus shown in FIG. 30 is used will be described as a first embodiment A, the case where the processing apparatus shown in FIG. 31 is used will be described as a first embodiment B, and the processing apparatus shown in FIG. Will be described as the first embodiment C, and the case where the processing apparatus shown in FIG. 33 is used will be described as the first embodiment D.

(第一の実施形態A)
図30に示す処理装置1は、密閉構造の容器20を処理槽7とし、容器20に収容可能な密閉構造の小容器21を対電極槽8とし、小容器21は少なくとも一部にイオン交換膜6を備えると共にガス(対電極10から発生するガス)を容器20の外に排出するガス排出管22を備えるものとしている。尚、図30に示す処理装置1では、対電極10と定電位設定装置12を結線する配線は、ガス排出管22の中を通過させているが、必ずしもこの構成には限定されず、配線をガス排出管22を通さずに定電位設定装置12と結線するようにしてもよい。
(First embodiment A)
In the processing apparatus 1 shown in FIG. 30, a sealed container 20 is used as a processing tank 7, a sealed small container 21 that can be accommodated in the container 20 is used as a counter electrode tank 8, and the small container 21 is at least partly an ion exchange membrane. 6 and a gas discharge pipe 22 for discharging gas (gas generated from the counter electrode 10) to the outside of the container 20. In the processing apparatus 1 shown in FIG. 30, the wiring connecting the counter electrode 10 and the constant potential setting device 12 passes through the gas exhaust pipe 22. However, the wiring is not necessarily limited to this configuration. The constant potential setting device 12 may be connected without passing through the gas discharge pipe 22.

したがって、図30に示す処理装置1によれば、処理槽7からバイオガスが漏洩することがない。また、対電極槽8から発生するガスが処理槽7に漏れ出すことがないので、バイオガスに対電極槽8から発生したガスが混入してバイオガスのメタン濃度を低下させたり、対電極槽8から発生したガスがメタン発酵液4に溶け込んでメタン発酵に関与する微生物群の生育や機能に悪影響を及ぼすこともない。さらに、処理槽7を密閉構造としているので、処理槽7を嫌気環境に制御し易い利点もある。   Therefore, according to the processing apparatus 1 shown in FIG. 30, biogas does not leak from the processing tank 7. In addition, since the gas generated from the counter electrode tank 8 does not leak into the processing tank 7, the gas generated from the counter electrode tank 8 is mixed with the biogas to reduce the methane concentration of the biogas, or the counter electrode tank. The gas generated from 8 does not dissolve in the methane fermentation solution 4 and does not adversely affect the growth and function of the microorganism group involved in methane fermentation. Furthermore, since the processing tank 7 has a sealed structure, there is an advantage that the processing tank 7 can be easily controlled in an anaerobic environment.

また、容器20に小容器21を収容することで、容器20に収容されているメタン発酵液4に小容器21が浸され、小容器21の少なくとも一部に備えられているイオン交換膜6はメタン発酵液4と接触する。換言すれば、メタン発酵液4はイオン交換膜6を介して電解液4aと接触する。   Moreover, by accommodating the small container 21 in the container 20, the small container 21 is immersed in the methane fermentation solution 4 accommodated in the container 20, and the ion exchange membrane 6 provided in at least a part of the small container 21 is Contact with methane fermentation solution 4. In other words, the methane fermentation solution 4 comes into contact with the electrolytic solution 4 a through the ion exchange membrane 6.

処理槽7としての密閉構造の容器20は、対電極槽8としての密閉構造の小容器21を収容可能な大きさの容器であり、形状は特に限定されない。容器の材質としては、例えば、ガラス、プラスチック、絶縁処理を施した金属、コンクリート等が挙げられるがこれらに限定されるものではない。また、ガス不透過性の膜材をヒートシール等により袋状に形成した容器を処理槽7として用いるようにしてもよい。   The container 20 having a sealed structure as the processing tank 7 is a container having a size capable of accommodating the small container 21 having the sealed structure as the counter electrode tank 8, and the shape thereof is not particularly limited. Examples of the material of the container include, but are not limited to, glass, plastic, an insulating metal, concrete, and the like. Further, a container in which a gas-impermeable film material is formed into a bag shape by heat sealing or the like may be used as the processing tank 7.

対電極槽8としての密閉構造の小容器21は、処理槽7としての容器20に収容可能な大きさの容器であり、少なくとも一部にイオン交換膜6を備えるものとしている。ここで、小容器21はその全体をイオン交換膜6で形成した袋状の容器としてもよいが、袋状の容器の片面だけをイオン交換膜6で構成したり、一つの面のさらに一部分をイオン交換膜6のみで構成するようにしてもよい。部分的にイオン交換膜6を用いる場合には、その他の部分は容器20と同様の上記材質で構成してもよいし、イオン交換膜6以外の膜材、例えばガス不透過性の膜材により構成し、小容器21からのガス(対電極槽8から発生するガス)が容器20の内部に漏洩しないようにしてもよい。   The small container 21 having a sealed structure as the counter electrode tank 8 is a container of a size that can be accommodated in the container 20 as the processing tank 7, and includes the ion exchange membrane 6 at least in part. Here, the small container 21 may be a bag-like container formed entirely by the ion-exchange membrane 6, but only one side of the bag-like container may be constituted by the ion-exchange membrane 6, or a part of one surface may be further formed. You may make it comprise only the ion exchange membrane 6. FIG. When the ion exchange membrane 6 is partially used, other portions may be made of the same material as that of the container 20, or may be made of a membrane material other than the ion exchange membrane 6, such as a gas-impermeable membrane material. It may be configured so that gas from the small container 21 (gas generated from the counter electrode tank 8) does not leak into the container 20.

有機性基質は、処理槽7に添加される。   The organic substrate is added to the treatment tank 7.

対電極槽8に収容される電解液4aは、例えば、ナトリウムイオンやカリウムイオン等を含むものとすればよい。尚、通常、メタン発酵液4にもナトリウムイオンやカリウムイオン等が含まれていることから、電解液4aとしてメタン発酵液4を用いることも可能である。   The electrolyte solution 4a accommodated in the counter electrode tank 8 may include, for example, sodium ions or potassium ions. In addition, since sodium ion, potassium ion, etc. are normally contained also in the methane fermentation liquid 4, it is also possible to use the methane fermentation liquid 4 as the electrolyte solution 4a.

作用電極9及び対電極10としては、例えば炭素板等の導電性材料を適宜使用することができる。対電極10では、作用電極9における酸化還元反応に対して電子の授受を補完する反応が進行する。   As the working electrode 9 and the counter electrode 10, for example, a conductive material such as a carbon plate can be used as appropriate. In the counter electrode 10, a reaction that complements the exchange of electrons with respect to the oxidation-reduction reaction in the working electrode 9 proceeds.

処理槽7の温度(メタン発酵液4の温度)は、4℃〜100℃未満とすればよいが、好適には40℃〜70℃、より好適には50℃〜60℃、さらに好適には55℃である。   The temperature of the treatment tank 7 (the temperature of the methane fermentation solution 4) may be 4 ° C to less than 100 ° C, but is preferably 40 ° C to 70 ° C, more preferably 50 ° C to 60 ° C, and even more preferably. 55 ° C.

本実施形態では、作用電極9の電位を作用電極9にて還元反応が生じ得る電位に制御しながらメタン発酵処理を行う。または、作用電極9の電位を銀・塩化銀電極電位基準で+0.3Vに制御しながらメタン発酵処理を行う。この際に、作用電極9の担体9aにメタン発酵に関与する微生物(例えば、水素資化性メタン菌や酢酸資化性メタン菌)等が担持されて活性化する。即ち、微生物群担持担体の作製が行われることになる。作用電極9にて還元反応が生じ得る電位について具体的に説明すると、作用電極9において還元反応を生じさせるために、作用電極9の電位を、作用電極9への電位無印加時のメタン発酵液4の溶液電位(酸化還元電位)よりもマイナス側に大きな電位に制御する。即ち、電位無印加時の作用電極9と参照電極11の間の電位差が、作用電極9への電位無印加時のメタン発酵液4の溶液電位に相当するので、その値よりもマイナス側に大きな電位を作用電極9に印加することで、作用電極9において還元反応を進行させることができる。具体的には、メタン発酵液が一般的に銀・塩化銀電極電位基準で−0.5V程度であることから、作用電極9の電位は−0.6Vを含んで−0.6Vよりもマイナス側に大きくすればよい。一方で、出来るだけ還元反応が強く生じる電位とした方が本発明の効果が得られやすくなると考えられるが、作用電極9の電位をマイナス側に大きくし過ぎると水の電気分解が激しく生じてメタン発酵が停止する虞があると共に、メタン発酵から水素発酵への移行が生じる虞もあるので、それよりも小さな電位とすることが好適である。但し、本実施形態のように、イオン交換膜6を備える場合には、メタン発酵から水素発酵への移行は生じ難い。また、−1.2V程度であれば水の電気分解が激しく生じることはない。したがって、−0.6V〜−1.2とすれば、本発明の効果を得られるものと考えられるが、−0.8V〜−1.0Vとすることが好適であり、−1.0Vとすることがより好適である。   In the present embodiment, the methane fermentation treatment is performed while controlling the potential of the working electrode 9 to a potential at which a reduction reaction can occur at the working electrode 9. Alternatively, the methane fermentation treatment is performed while controlling the potential of the working electrode 9 to +0.3 V with reference to the silver / silver chloride electrode potential. At this time, microorganisms (for example, hydrogen-utilizing methane bacteria or acetic acid-assimilating methane bacteria) involved in methane fermentation are supported on the carrier 9a of the working electrode 9 and activated. That is, production of a microorganism group-supporting carrier is performed. The potential at which the reduction reaction can occur at the working electrode 9 will be described in detail. In order to cause the reduction reaction at the working electrode 9, the potential of the working electrode 9 is changed to a methane fermentation solution when no potential is applied to the working electrode 9. 4 is controlled to a potential larger on the minus side than the solution potential (oxidation-reduction potential). That is, the potential difference between the working electrode 9 and the reference electrode 11 when no potential is applied corresponds to the solution potential of the methane fermentation broth 4 when no potential is applied to the working electrode 9, and is therefore larger on the minus side than that value. By applying a potential to the working electrode 9, the reduction reaction can proceed at the working electrode 9. Specifically, since the methane fermentation liquid is generally about −0.5 V on the basis of the silver / silver chloride electrode potential, the potential of the working electrode 9 includes −0.6 V and is minus −0.6 V. You just need to make it bigger. On the other hand, it is considered that the potential of the present invention can be obtained more easily when the potential at which the reduction reaction is as strong as possible. However, if the potential of the working electrode 9 is increased too much to the minus side, water electrolysis occurs vigorously and methane Since there is a possibility that fermentation may stop and there is a possibility that transition from methane fermentation to hydrogen fermentation may occur, it is preferable to use a potential lower than that. However, when the ion exchange membrane 6 is provided as in this embodiment, the transition from methane fermentation to hydrogen fermentation hardly occurs. Moreover, if it is about -1.2V, electrolysis of water will not occur violently. Therefore, it can be considered that the effect of the present invention can be obtained by setting −0.6 V to −1.2, but −0.8 V to −1.0 V is preferable, and −1.0 V is preferable. More preferably.

本発明の効果は、イオン交換膜6を備えることで得られ易くなる。つまり、本発明の微生物群担持担体からはメタン発酵液への微生物の供給が行われると共に、メタン発酵液には元々メタン発酵に関与する微生物が存在しており、イオン交換膜6を備えることで、メタン発酵液4に存在する微生物を対電極槽8に移動(拡散)させることなく、処理槽7側に留めることができる。したがって、対電極10の酸化反応に伴う微生物からの電子の引き抜きを防ぎながら、作用電極9から微生物へ電子を供給することができるので、本発明の効果をより得られ易くなる。さらには、対電極槽8に電解液を入れておくことで、対電極槽8による電子の引き抜き反応が電解液との間で完結するので、微生物からの電子の引き抜きが確実に防止される。   The effect of the present invention is easily obtained by providing the ion exchange membrane 6. That is, the microorganism group-supporting carrier of the present invention supplies microorganisms to the methane fermentation solution, and the methane fermentation solution originally contains microorganisms that are involved in methane fermentation, and includes the ion exchange membrane 6. The microorganisms present in the methane fermentation liquid 4 can be retained on the treatment tank 7 side without being moved (diffused) to the counter electrode tank 8. Therefore, since the electrons can be supplied from the working electrode 9 to the microorganism while preventing the electrons from being extracted from the microorganism due to the oxidation reaction of the counter electrode 10, the effect of the present invention can be obtained more easily. Furthermore, by putting the electrolytic solution in the counter electrode tank 8, the electron extraction reaction by the counter electrode tank 8 is completed with the electrolytic solution, so that the extraction of electrons from the microorganisms is reliably prevented.

また、イオン交換膜6を備えることで、作用電極9の電位を制御したときに、メタン発酵液4と電解液4aとの間でのイオン電流の流れが許容されるので、メタン発酵液4の電荷バランスを維持しながら、作用電極9の電位を制御し続けることができる。   Further, by providing the ion exchange membrane 6, when the potential of the working electrode 9 is controlled, the flow of ion current between the methane fermentation solution 4 and the electrolytic solution 4a is allowed. The potential of the working electrode 9 can be continuously controlled while maintaining the charge balance.

ここで、本発明では、担体保持電極の担体に微生物が十分に付着することから、作用電極9の近傍の溶液電位のみを制御できれば、担体に担持した微生物にとって至適な電位環境に制御することができ、微生物に電子が供給されてメタン発酵に関与する微生物コミュニティーを安定に維持することができる。したがって、溶液電位を制御するために一般的に用いられる酸化還元物質(鉄イオン錯体、フェロシアン化カリウム、アントラキノンジスルホン酸ナトリウムなどのキノン化合物、メチルビオロゲン)のような高価な試薬を一切添加する必要が無い点において極めて優れたものである。   Here, in the present invention, since microorganisms adhere sufficiently to the carrier of the carrier holding electrode, if only the solution potential in the vicinity of the working electrode 9 can be controlled, the potential environment can be controlled to be optimal for the microorganisms supported on the carrier. The microbial community involved in methane fermentation can be stably maintained by supplying electrons to the microorganism. Therefore, it is not necessary to add any expensive reagents such as redox substances (quinone compounds such as iron ion complex, potassium ferrocyanide, sodium anthraquinone disulfonate, methyl viologen) that are generally used to control the solution potential. It is very excellent in terms.

(第一の実施形態B) (First embodiment B)

図31に示す処理装置1は、上方が開放されている容器23をイオン交換膜6で仕切ることにより開放された二つの槽が形成され、処理槽7としての一方の槽の上方開放部がガス不透過膜またはガス不透過部材24により塞がれているものとしている。つまり、図31に示す処理装置1は、対電極槽8から発生するガスを処理槽7に漏れ出さないようにする構成以外は、図30と同一の構成としている。したがって、図30に示す処理装置を用いた場合と同様の効果が得られる。   In the processing apparatus 1 shown in FIG. 31, two tanks opened by partitioning a container 23 whose upper side is opened by an ion exchange membrane 6 are formed, and an upper open part of one tank as the processing tank 7 is a gas. It is assumed that it is blocked by an impermeable film or a gas impermeable member 24. That is, the processing apparatus 1 shown in FIG. 31 has the same configuration as that of FIG. 30 except that the gas generated from the counter electrode tank 8 does not leak into the processing tank 7. Therefore, the same effect as that obtained when the processing apparatus shown in FIG. 30 is used can be obtained.

ガス不透過膜またはガス不透過部材24としては、各種分野で一般に用いられているものを適宜用いることができる。例えば、ガス不透過部材としては、ガラス、プラスチック、絶縁処理を施した金属、コンクリート等が挙げられるがこれらに限定されるものではない。また、ガス不透過膜としては、例えばイオン交換膜6を用いることができるがこれに限定されるものではない。   As the gas impermeable film or the gas impermeable member 24, those generally used in various fields can be appropriately used. For example, examples of the gas impermeable member include, but are not limited to, glass, plastic, an insulating metal, concrete, and the like. Further, as the gas impermeable membrane, for example, an ion exchange membrane 6 can be used, but is not limited thereto.

尚、対電極槽8については、開放したままでもよいが、処理槽7と同様に密閉構造とし、対電極槽8において発生するガスを対電極槽8の外に排出するガス排出管を備えるようにしてもよい。この場合には、対電極槽8から発生するガスを所望の位置から排出させることができるので、これを回収し、場合によっては再利用することが可能となる。   The counter electrode tank 8 may be left open, but has a sealed structure like the processing tank 7 and includes a gas discharge pipe for discharging the gas generated in the counter electrode tank 8 out of the counter electrode tank 8. It may be. In this case, since the gas generated from the counter electrode tank 8 can be discharged from a desired position, it can be recovered and reused in some cases.

(第一の実施形態C)
図32に示す処理装置1は、収容される液体の液面よりも下部に開口部を備える二つの容器25aと25bがイオン交換膜6を介して開口部で連結されてU字型の容器25が形成され、一方の容器25aを密閉構造として処理槽7とし、他方の容器25bを開放して対電極槽8としている。この場合、メタン発酵液4と電解液4aがイオン交換膜6を介して接触すると共に、処理槽7のメタン発酵液4の液面よりも上部の空間と対電極槽8の電解液4aの液面よりも上部の空間とが容器25自体のU字型構造によって隔てて配置される。そして、一方の容器25aが密閉構造とされていることから、対電極槽8から発生するガスが処理槽7に侵入するのを防ぎながら、処理槽7から発生するバイオガスが処理槽7から漏洩するのを防ぐことができる。したがって、図30に示す処理装置を用いた場合と同様の効果が得られる。
(First embodiment C)
In the processing apparatus 1 shown in FIG. 32, two containers 25a and 25b each having an opening below the liquid level of the liquid to be accommodated are connected to each other through the opening via the ion exchange membrane 6, and a U-shaped container 25 is used. The one container 25a is used as a processing tank 7 with a sealed structure, and the other container 25b is opened as a counter electrode tank 8. In this case, the methane fermentation solution 4 and the electrolyte solution 4a are in contact with each other via the ion exchange membrane 6, and the space above the liquid surface of the methane fermentation solution 4 in the treatment tank 7 and the solution of the electrolyte solution 4a in the counter electrode tank 8 are used. The space above the surface is spaced apart by the U-shaped structure of the container 25 itself. And since one container 25a is made into the airtight structure, the biogas generated from the processing tank 7 leaks from the processing tank 7 while preventing the gas generated from the counter electrode tank 8 from entering the processing tank 7. Can be prevented. Therefore, the same effect as that obtained when the processing apparatus shown in FIG. 30 is used can be obtained.

尚、図32に示す処理装置1における他方の容器25bの開放とは、例えば他方の容器25bの端部を完全に開放した場合は勿論のこと、一方の容器25aと同様に密閉構造としつつ、対電極槽8において発生するガスを対電極槽8の外に排出するガス排出管を備える場合も含むことを意味している。ガス排出管を備える場合には、対電極槽8から発生するガスを所望の位置から排出させることができるので、これを回収して再利用し易くなる。   In addition, the opening of the other container 25b in the processing apparatus 1 shown in FIG. 32 means that, for example, when the end of the other container 25b is completely opened, the sealing structure is the same as that of the one container 25a. This also includes the case where a gas discharge pipe for discharging the gas generated in the counter electrode tank 8 to the outside of the counter electrode tank 8 is provided. When the gas discharge pipe is provided, the gas generated from the counter electrode tank 8 can be discharged from a desired position, so that it can be easily recovered and reused.

(第一の実施形態D)
図33に示す処理装置1は、収容される液体の液面よりも下部に開口部を備える二つの容器26aと26bがイオン交換膜6を介して開口部で連結されてH字型の容器26が形成され、一方の容器26aを密閉構造として処理槽7とし、他方の容器26bを開放して対電極槽8としている。この場合にも、メタン発酵液4と電解液4aがイオン交換膜6を介して接触すると共に、処理槽7のメタン発酵液4の液面よりも上部の空間と対電極槽8の電解液4aの液面よりも上部の空間とが容器26自体のH字型構造によって隔てて配置される。そして、H字型容器26の一方の容器26aが密閉構造とされていることから、処理槽7は密閉構造となる。したがって、対電極槽8から発生するガスが処理槽7に侵入するのを防ぎながら、処理槽7から発生するバイオガスが処理槽7から漏洩するのを防ぐことができる。したがって、図30に示す処理装置を用いた場合と同様の効果が得られる。
(First embodiment D)
In the processing apparatus 1 shown in FIG. 33, two containers 26a and 26b each having an opening below the liquid level of the liquid to be accommodated are connected by an opening through the ion exchange membrane 6, and an H-shaped container 26 is provided. The one container 26a has a sealed structure as the processing tank 7, and the other container 26b is opened as the counter electrode tank 8. In this case as well, the methane fermentation solution 4 and the electrolyte solution 4a are in contact with each other through the ion exchange membrane 6, and the space above the liquid surface of the methane fermentation solution 4 in the treatment tank 7 and the electrolyte solution 4a in the counter electrode tank 8 are used. The space above the liquid level is spaced apart by the H-shaped structure of the container 26 itself. And since one container 26a of the H-shaped container 26 is made into the sealed structure, the processing tank 7 becomes a sealed structure. Therefore, it is possible to prevent the biogas generated from the processing tank 7 from leaking from the processing tank 7 while preventing the gas generated from the counter electrode tank 8 from entering the processing tank 7. Therefore, the same effect as that obtained when the processing apparatus shown in FIG. 30 is used can be obtained.

尚、本実施形態における他方の容器26bの開放とは、容器26を完全に開放した場合は勿論のこと、一方の容器26aと同様に密閉構造としつつ、対電極槽8において発生するガスを対電極槽8の外に排出するガス排出管を備える場合も含むことを意味している。ガス排出管を備える場合には、対電極槽8から発生するガスを所望の位置から排出させることができるので、これを回収して再利用し易くなる。   In the present embodiment, the opening of the other container 26b is not limited to the case where the container 26 is completely opened. This also includes the case where a gas discharge pipe for discharging outside the electrode tank 8 is provided. When the gas discharge pipe is provided, the gas generated from the counter electrode tank 8 can be discharged from a desired position, so that it can be easily recovered and reused.

<第二の実施形態>
第二の実施形態にかかるメタン発酵方法は、電極表面の少なくとも一部に微生物を担持し得る疎水性の担体を備えた担体保持電極を作用電極とし、作用電極と対電極と参照電極とを定電位設定装置に結線し、メタン発酵液と対電極とをイオン交換膜を介して接触させ、メタン発酵液に作用電極と参照電極とを接触させ、作用電極の電位を3電極方式で制御するようにしている。つまり、第一の実施形態におけるメタン発酵方法とは、電解液を用いることなく対電極を直接イオン交換膜に接触させている点のみが異なっている。
<Second Embodiment>
In the methane fermentation method according to the second embodiment, a carrier holding electrode including a hydrophobic carrier capable of supporting microorganisms on at least a part of an electrode surface is used as a working electrode, and a working electrode, a counter electrode, and a reference electrode are defined. It is connected to the potential setting device, the methane fermentation broth and the counter electrode are brought into contact with each other through an ion exchange membrane, the working electrode and the reference electrode are brought into contact with the methane fermentation broth, and the potential of the working electrode is controlled by a three-electrode system. I have to. That is, the methane fermentation method in the first embodiment is different from the methane fermentation method only in that the counter electrode is brought into direct contact with the ion exchange membrane without using an electrolytic solution.

しかしながら、第一の実施形態のように電解液4aを用いずとも、作用電極9と対電極10との間でイオン交換膜6を介してイオン電流は流れる。また、メタン発酵液4中の微生物を対電極10側に移動(拡散)させることなく、処理槽7に留める効果も得られる。したがって、第二の実施形態にかかるメタン発酵方法によれば、第一の実施形態と同様の電位制御条件で、同様の効果を得ることが可能である。   However, an ion current flows between the working electrode 9 and the counter electrode 10 via the ion exchange membrane 6 without using the electrolytic solution 4a as in the first embodiment. Further, the effect of retaining the microorganisms in the methane fermentation solution 4 in the treatment tank 7 without moving (diffusing) to the counter electrode 10 side is also obtained. Therefore, according to the methane fermentation method according to the second embodiment, the same effect can be obtained under the same potential control conditions as in the first embodiment.

第二の実施形態にかかるメタン発酵方法は、例えば図34に示す処理装置により実施される。図34に示す処理装置1は、イオン交換膜6を少なくとも一部に備える密閉構造の容器5内に作用電極9と参照電極11が配置され、容器5の外側に対電極10が配置され、容器5にメタン発酵液4が収容されると共に作用電極9と参照電極11がメタン発酵液4に浸され、容器4のイオン交換膜6は容器5にメタン発酵液4が収容されたときに少なくともその一部がイオン交換膜6と接触しうる位置に備えられ、イオン交換膜6のメタン発酵液4の接触面とは反対側の面の少なくとも一部に対電極10が接触して配置されているものとしている。図34に示す処理装置1では、容器5のメタン発酵液4の液面よりも下部に開口部5aが設けられ、開口部5aがイオン交換膜6で塞がれ、容器5の外側のイオン交換膜6の表面の少なくとも一部に対電極10が接触して配置されているものとしている。つまり、図34に示す処理装置1では、容器5全体が処理槽7として機能することとなる。   The methane fermentation method according to the second embodiment is performed by, for example, a processing apparatus shown in FIG. The processing apparatus 1 shown in FIG. 34 has a working electrode 9 and a reference electrode 11 arranged in a sealed container 5 having at least a part of an ion exchange membrane 6, and a counter electrode 10 arranged outside the container 5. 5, the working electrode 9 and the reference electrode 11 are immersed in the methane fermentation solution 4, and the ion exchange membrane 6 of the container 4 is at least when the methane fermentation solution 4 is stored in the container 5. The counter electrode 10 is disposed in contact with at least a part of the surface of the ion exchange membrane 6 opposite to the contact surface of the methane fermentation broth 4, provided in a position where a part can be in contact with the ion exchange membrane 6. It is supposed to be. In the processing apparatus 1 shown in FIG. 34, an opening 5 a is provided below the liquid level of the methane fermentation solution 4 in the container 5, the opening 5 a is closed with the ion exchange membrane 6, and ion exchange outside the container 5 is performed. It is assumed that the counter electrode 10 is disposed in contact with at least a part of the surface of the film 6. That is, in the processing apparatus 1 shown in FIG. 34, the entire container 5 functions as the processing tank 7.

したがって、図34に示す処理装置1によれば、容器5からバイオガスが漏洩することがない。また、対電極10から発生するガスが容器5内に漏れ出すことがないので、バイオガスに対電極10から発生したガスが混入してバイオガスのメタン濃度を低下させたり、対電極10から発生したガスがメタン発酵液4に溶け込んでメタン発酵に関与する微生物群の生育や機能に悪影響を及ぼすこともない。さらに、容器5を密閉構造としているので、容器5内を嫌気環境に制御し易い利点もある。   Therefore, according to the processing apparatus 1 shown in FIG. 34, biogas does not leak from the container 5. Further, since the gas generated from the counter electrode 10 does not leak into the container 5, the gas generated from the counter electrode 10 is mixed into the biogas to reduce the methane concentration of the biogas, or from the counter electrode 10. The dissolved gas does not dissolve in the methane fermentation solution 4 and does not adversely affect the growth and function of the microorganism group involved in methane fermentation. Furthermore, since the container 5 has a sealed structure, there is an advantage that the inside of the container 5 can be easily controlled in an anaerobic environment.

尚、図34に示す処理装置1では、第一の実施形態と同様に、ガス回収手段15、メタン発酵液採取手段16を備えるようにしているが、上記の通り、ガス回収方法、メタン発酵液採取方法は、これらの手段を利用したものには限定されない。また、第一の実施形態と同様、メタン発酵液4に物質を添加・供給する手段を設けるようにしてもよい。   In addition, although the processing apparatus 1 shown in FIG. 34 includes the gas recovery means 15 and the methane fermentation liquid collection means 16 as in the first embodiment, as described above, the gas recovery method, the methane fermentation liquid The collection method is not limited to those using these means. Moreover, you may make it provide the means to add and supply a substance to the methane fermentation liquid 4 similarly to 1st embodiment.

以下、図34に示す処理装置1の詳細について説明する。但し、以下に説明する以外の構成については、第一の実施形態と実質的に同一であり、説明は省略する。   Hereinafter, the details of the processing apparatus 1 shown in FIG. 34 will be described. However, configurations other than those described below are substantially the same as those in the first embodiment, and a description thereof will be omitted.

容器5は、イオン交換膜6を少なくとも一部に備える密閉構造としている。容器5の材質としては、例えば、ガラス、プラスチック、絶縁処理を施した金属、コンクリート等が挙げられるがこれらに限定されるものではない。尚、図34では、密閉構造の容器5のメタン発酵液4の液面よりも下部に設けられた開口部5aをイオン交換膜6により塞ぐようにしているが、容器5の形態や構造は特に限定されない。例えば容器5全体をイオン交換膜6で形成した袋状の容器としてもよいし、袋状の容器の片面だけをイオン交換膜6で構成してもよいし、一つの面のさらに一部分をイオン交換膜6のみで構成するようにしてもよい。部分的にイオン交換膜6を用いる場合には、その他の部分はガラス等の上記材質で構成してもよいし、イオン交換膜6以外の膜材、例えばメタン発酵液4とメタン発酵液4中の成分(微生物を含む)の双方を透過させることがない膜材により構成してもよい。要は、容器5に収容されるメタン発酵液4が容器5の少なくとも一部を構成するイオン交換膜6と接触しうる構造の容器とすればよい。   The container 5 has a sealed structure including at least a part of the ion exchange membrane 6. Examples of the material of the container 5 include, but are not limited to, glass, plastic, metal subjected to insulation treatment, concrete, and the like. In FIG. 34, the opening 5a provided below the liquid surface of the methane fermentation solution 4 of the sealed container 5 is closed by the ion exchange membrane 6. However, the form and structure of the container 5 are not particularly limited. It is not limited. For example, the entire container 5 may be a bag-shaped container formed of the ion-exchange membrane 6, or only one surface of the bag-shaped container may be formed of the ion-exchange membrane 6, or a part of one surface may be ion-exchanged. You may make it comprise only with the film | membrane 6. FIG. When the ion exchange membrane 6 is partially used, the other portions may be made of the above-mentioned material such as glass, or other membrane materials other than the ion exchange membrane 6, such as the methane fermentation broth 4 and the methane fermentation broth 4 You may comprise with the film | membrane material which does not permeate | transmit both of the component (including microorganisms). In short, the methane fermentation solution 4 accommodated in the container 5 may be a container having a structure that can come into contact with the ion exchange membrane 6 constituting at least a part of the container 5.

対電極10は、イオン交換膜6のメタン発酵液4との接触面とは反対側の面の少なくとも一部に接触させるようにしている。本実施形態において、対電極10は板状の炭素電極としているが、対電極10の形状と材質はこれに限定されるものではなく、要は、イオン交換膜6との接触が可能な形状であり、且つ作用電極9における酸化還元反応に対して電子の授受を補完する反応を進行させることが可能な材質、つまり、作用電極9において還元反応が生じる際に酸化反応を進行させることが可能な材質の電極とすればよい。また、本実施形態では、対電極10の面積をイオン交換膜6の面積よりも大きなものとしてイオン交換膜6全体を対電極10で完全に覆うようにし、イオン交換膜6と対電極10とを接触させるようにしているが、イオン交換膜6のメタン発酵液4との接触面とは反対側の面の少なくとも一部に対電極10を接触させれば、イオン交換膜6を介してメタン発酵液4から対電極10にイオンが伝達するので、必ずしもイオン交換膜6全体を対電極10で完全に覆うようにしてイオン交換膜6と対電極10とを接触させずともよい。但し、イオン交換膜6全体を対電極10で完全に覆うことで、対電極10をイオン交換膜6の保護材としても機能させることができると共に、メタン発酵液4からのイオンの伝達面が増大する結果として、メタン発酵液4の電位制御性を高めることができる利点があり、好適である。イオン交換膜6全体を対電極10で完全に覆う方法としては、例えば、容器5の開口部5aの周囲に接着剤を塗布して対電極10を接着することにより、開口部5aを塞ぐイオン交換膜6全体と対電極10とを接触させるようにしてもよいし、容器5の開口部5aの周囲に接着剤を塗布して対電極10の表面の少なくとも一部に塗布形成されたイオン交換膜6を接着することにより、開口部5aをイオン交換膜6で塞ぎつつ、開口部5aを塞ぐイオン交換膜6全体と対電極10とを接触させるようにしてもよい。イオン交換膜6を塗布形成するための薬剤としては、例えばナフィオン分散液が挙げられるが、これに限定されるものではない。また、対電極10の表面にナフィオン分散液を塗布し、ナフィオン分散液が乾燥する前にイオン交換膜6を貼り付けるようにしてもよい。この場合には、イオン交換膜6の対電極10の表面への接着性と接触性とを十分なものとすることができる。   The counter electrode 10 is brought into contact with at least a part of the surface opposite to the contact surface of the ion exchange membrane 6 with the methane fermentation solution 4. In the present embodiment, the counter electrode 10 is a plate-like carbon electrode, but the shape and material of the counter electrode 10 are not limited to this, and the shape is that the contact with the ion exchange membrane 6 is essential. And a material capable of proceeding with a reaction that complements the exchange of electrons with respect to the oxidation-reduction reaction at the working electrode 9, that is, the oxidation reaction can proceed when the reduction reaction occurs at the working electrode 9. A material electrode may be used. In the present embodiment, the counter electrode 10 has a larger area than the ion exchange membrane 6 so that the entire ion exchange membrane 6 is completely covered with the counter electrode 10, and the ion exchange membrane 6 and the counter electrode 10 are covered. Although it is made to contact, if the counter electrode 10 is made to contact at least one part of the surface on the opposite side to the contact surface of the ion exchange membrane 6 with the methane fermentation liquid 4, methane fermentation will be carried out via the ion exchange membrane 6. Since ions are transmitted from the liquid 4 to the counter electrode 10, the ion exchange membrane 6 and the counter electrode 10 do not necessarily have to be in contact with each other so that the entire ion exchange membrane 6 is completely covered with the counter electrode 10. However, by completely covering the entire ion exchange membrane 6 with the counter electrode 10, the counter electrode 10 can function as a protective material for the ion exchange membrane 6, and the ion transmission surface from the methane fermentation solution 4 is increased. As a result, there is an advantage that the potential controllability of the methane fermentation broth 4 can be improved, which is preferable. As a method of completely covering the entire ion exchange membrane 6 with the counter electrode 10, for example, ion exchange is performed by closing the opening 5 a by applying an adhesive around the opening 5 a of the container 5 and bonding the counter electrode 10. The entire membrane 6 and the counter electrode 10 may be brought into contact with each other, or an ion exchange membrane formed by applying an adhesive around the opening 5a of the container 5 and applying it to at least a part of the surface of the counter electrode 10 By bonding 6, the counter electrode 10 may be brought into contact with the entire ion exchange membrane 6 that closes the opening 5 a while closing the opening 5 a with the ion exchange membrane 6. Examples of the agent for coating and forming the ion exchange membrane 6 include a Nafion dispersion, but are not limited thereto. Alternatively, a Nafion dispersion may be applied to the surface of the counter electrode 10 and the ion exchange membrane 6 may be attached before the Nafion dispersion is dried. In this case, the adhesion and contact properties of the ion exchange membrane 6 to the surface of the counter electrode 10 can be made sufficient.

ここで、対電極10は多孔質体とすることが好適である。この場合には、イオン交換膜6と対電極10との接触面で発生したガスを接触面とは反対側の面に通過させやすくなる。尚、対電極10を多孔質体とし、ナフィオン分散液を用いてイオン交換膜6を貼り付けることで、ナフィオン分散液の多孔質体の孔への侵入によりイオン交換膜6と対電極10との接触面積を増大させて電気化学反応をより進行させやすくすることができ、好適である。   Here, the counter electrode 10 is preferably a porous body. In this case, the gas generated at the contact surface between the ion exchange membrane 6 and the counter electrode 10 can easily pass through the surface opposite to the contact surface. In addition, the counter electrode 10 is made a porous body, and the ion exchange membrane 6 is attached using a Nafion dispersion liquid, whereby the ion exchange membrane 6 and the counter electrode 10 are separated by the penetration of the Nafion dispersion liquid into the pores of the porous body. The contact area can be increased to facilitate the progress of the electrochemical reaction, which is preferable.

ここで、上述の第一の実施形態及び第二の実施形態においては、メタン発酵処理が行われるのと同時に、微生物群担持担体の作製も行われる。微生物群担持担体は、引き続きメタン発酵液4に接触させたまま作用電極9として使用し、本発明のメタン発酵処理を行うことが好適である。この場合、作製した微生物群担持担体を取り出すことなく、そのままメタン発酵処理を継続できる。また、メタン発酵液4に生息する微生物の量や分布も電位制御によってメタン発酵に適したものとなっているので、その恩恵を受けながら、メタン発酵処理を行うことができる。勿論、上記により作製した微生物群担持担体を一旦取り出して、別のメタン発酵槽のメタン発酵液に入れてメタン発酵処理を行っても良いし、さらに微生物群担持担体に電位を印加して、メタン発酵処理を行うようにしてもよい。   Here, in the first embodiment and the second embodiment described above, the microbial fermentation treatment is performed, and at the same time, the microorganism group-supporting carrier is also produced. It is preferable that the microorganism group-supporting carrier is used as the working electrode 9 while being kept in contact with the methane fermentation solution 4 and performing the methane fermentation treatment of the present invention. In this case, the methane fermentation treatment can be continued as it is without taking out the produced microorganism group-supporting carrier. Moreover, since the quantity and distribution of microorganisms inhabiting the methane fermentation liquid 4 are also suitable for methane fermentation by controlling the potential, the methane fermentation treatment can be performed while receiving the benefits. Of course, the microorganism group-supported carrier prepared as described above may be once taken out and placed in a methane fermentation solution in another methane fermentation tank to perform methane fermentation treatment. You may make it perform a fermentation process.

上述の形態は本発明の好適な形態の一例ではあるがこれに限定されるものではなく本発明の要旨を逸脱しない範囲において種々変形実施可能である。例えば、本発明を実施するための処理装置は、例えば図35に示すように、メタン発酵液4と電解質4aをイオン交換膜6ではなく、イオンや微生物を一切透過させることのない不透過部材40で隔て、あるいは処理槽7と対電極槽8を別の容器で形成し、塩橋41(寒天等にKCl等の飽和電解質溶液を入れたもの)を介してメタン発酵液4と電解質4aを接触(液絡)させるようにしてもよい。この場合にも、メタン発酵液4中の微生物の対電極槽8への移動を防ぐことができるので、対電極10からの電子の引き抜きを防ぐことができ、しかも、塩橋によってイオン電流の流れが許容される。また、メタン発酵液4に含まれる酸化還元物質3についても対電極槽8に透過しないので、メタン発酵液4の溶液電位の制御性も確保される。   The above-described embodiment is an example of a preferred embodiment of the present invention, but is not limited thereto, and various modifications can be made without departing from the gist of the present invention. For example, as shown in FIG. 35, for example, the processing apparatus for carrying out the present invention is not an ion-exchange membrane 6 but an impervious member 40 that does not allow ions or microorganisms to permeate through the methane fermentation solution 4 and the electrolyte 4a. Or the treatment tank 7 and the counter electrode tank 8 are formed in separate containers, and the methane fermentation solution 4 and the electrolyte 4a are brought into contact with each other through a salt bridge 41 (agar or the like containing a saturated electrolyte solution such as KCl). (Liquid junction) may be used. Also in this case, since the movement of microorganisms in the methane fermentation broth 4 to the counter electrode tank 8 can be prevented, the extraction of electrons from the counter electrode 10 can be prevented, and the flow of ion current by the salt bridge can be prevented. Is acceptable. In addition, since the redox material 3 contained in the methane fermentation broth 4 does not pass through the counter electrode tank 8, the controllability of the solution potential of the methane fermentation broth 4 is also ensured.

また、上述の実施形態では、電極表面の少なくとも一部に微生物を担持し得る担体を備えた担体保持電極を用いるようにしているが、微生物を担持し得る担体を電極表面の一部に備えることなく、電極から離して(即ち、担体を電極に付着させることなく培養液または発酵液に分散させて)本発明の生物学的処理方法またはメタン発酵処理方法を実施するようにしてもよい。この場合にも、電極による溶液電位の制御によって、本発明と同様に、高負荷条件下においても優れた処理能力を発揮し、目的の処理を効率よく実施することが可能となり得る。   In the above-described embodiment, the carrier holding electrode including a carrier capable of supporting microorganisms is used on at least a part of the electrode surface. However, a carrier capable of supporting microorganisms is provided on a part of the electrode surface. Alternatively, the biological treatment method or the methane fermentation treatment method of the present invention may be performed separately from the electrode (that is, by dispersing the carrier in the culture solution or the fermentation solution without adhering to the electrode). In this case as well, by controlling the solution potential with the electrode, it is possible to exhibit an excellent processing capability even under a high load condition and to efficiently perform the target processing, as in the present invention.

さらに、上述の実施形態では、電極表面の少なくとも一部に微生物を担持し得る担体を備えた担体保持電極を用いながらも、微生物を担持し得る担体を培養液または発酵液に分散させて本発明の生物学的処理方法またはメタン発酵処理方法を実施するようにしてもよい。このように、微生物を担持し得る担体を培養液中または発酵液中と電極表面の双方に備えることによって、培養液中または発酵液中と電極表面の双方の担体にて微生物を活性化させ、さらなる高負荷条件下においても優れた処理能力を発揮し、目的の処理をさらに効率よく実施することが可能となり得る。   Furthermore, in the above-described embodiment, while using a carrier holding electrode provided with a carrier capable of supporting microorganisms on at least a part of the electrode surface, the carrier capable of supporting microorganisms is dispersed in a culture solution or a fermentation solution, and the present invention is performed. The biological treatment method or the methane fermentation treatment method may be carried out. Thus, by providing a carrier capable of supporting microorganisms in the culture solution or both in the fermentation broth and on the electrode surface, the microorganisms are activated in the culture solution or in both the fermentation broth and the electrode surface, It may be possible to exhibit an excellent processing capacity even under higher load conditions and to perform the target processing more efficiently.

以下に本発明の実施例を説明するが、本発明はこれら実施例に限られるものではない。   Examples of the present invention will be described below, but the present invention is not limited to these examples.

まず、参考例として、微生物を担持し得る担体を保持していない電極を用いた場合の実験結果を以下に示す。   First, as a reference example, the experimental results when using an electrode that does not hold a carrier capable of supporting microorganisms are shown below.

(参考例A−1)
1.実験装置及び実験方法
本参考例において使用した実験装置の断面図を図1に示す。250mL容の2つのガラスバイアル瓶(Duran製)のうちの一方をメタン発酵槽26aとし、他方を対電極槽26bとし、下部開口部において陽イオン交換膜(ナフィオンK)を介して2つのバイアル瓶を接続し、H字型の容器26とした。また、メタン発酵槽26aには排出部51と供給部52を設けた。メタン発酵槽26aには蓋をし、蓋の上面にはシリコーンゴム栓を設けて、配線や電極を通した際の密閉製を確保した。また、蓋の上面のシリコーンゴム栓に管33を通し、メタン発酵槽26aの発酵液4の液面の上部の空間(ヘッドスペース)のガスを管33の一端から排出して、管の他端に接続された袋34にガスを回収するようにした。
(Reference Example A-1)
1. Experimental Apparatus and Experimental Method FIG. 1 shows a cross-sectional view of the experimental apparatus used in this reference example. One of two 250 mL glass vials (manufactured by Duran) is the methane fermentation tank 26a, the other is the counter electrode tank 26b, and the two vials via a cation exchange membrane (Nafion K) at the lower opening. Were connected to form an H-shaped container 26. Moreover, the discharge part 51 and the supply part 52 were provided in the methane fermentation tank 26a. The methane fermentation tank 26a was covered, and a silicone rubber stopper was provided on the upper surface of the lid to ensure a sealed product when wiring and electrodes were passed. Further, the pipe 33 is passed through the silicone rubber stopper on the upper surface of the lid, and the gas in the space (head space) above the liquid level of the fermentation liquid 4 in the methane fermentation tank 26a is discharged from one end of the pipe 33, and the other end of the pipe Gas was collected in the bag 34 connected to the.

対電極槽26bには、電解液4aを収容すると共に対電極10(2.5cm×7.5cm×0.3cmの板状炭素電極)を収容して電解液4aに浸した。対電極槽26bも蓋をし、蓋の上面にはシリコーンゴム栓を設けて、シリコーンゴム栓にガス排出管22を貫通させた。そして、対電極10と電位制御装置12を結線するための配線31をガス排出管22に通した。ガス排出管22は両端が開口されており、一端を対電極槽26bの内部に、他端を対電極槽26bの外側に配置するようにして、対電極槽26bで発生するガスが対電極槽26bの外側に排出されるようにした。   The counter electrode tank 26b accommodated the electrolyte solution 4a and the counter electrode 10 (2.5 cm × 7.5 cm × 0.3 cm plate-like carbon electrode), and was immersed in the electrolyte solution 4a. The counter electrode tank 26b was also covered, and a silicone rubber plug was provided on the upper surface of the cover, and the gas discharge pipe 22 was passed through the silicone rubber plug. Then, a wiring 31 for connecting the counter electrode 10 and the potential control device 12 was passed through the gas exhaust pipe 22. Both ends of the gas discharge pipe 22 are opened, and the gas generated in the counter electrode tank 26b is arranged so that one end is disposed inside the counter electrode tank 26b and the other end is disposed outside the counter electrode tank 26b. It was made to discharge to the outside of 26b.

作用電極9(2.5cm×7.5cm×0.3cmの板状炭素電極)は、メタン発酵槽26aに収容して発酵液4に浸し、作用電極9から電位制御装置12への配線はシリコーンゴム栓を通してメタン発酵槽26aの外側に引き出した。参照電極11(銀・塩化銀電極)はメタン発酵槽26aの外側からシリコーンゴム栓に差し込んで、発酵液4と接触させた。作用電極9と対電極10と参照電極11とを3電極式の電位制御装置(ポテンシオスタット)12に結線して、作用電極9の電位を制御した。   The working electrode 9 (2.5 cm × 7.5 cm × 0.3 cm plate-like carbon electrode) is housed in the methane fermentation tank 26a and immersed in the fermentation broth 4, and the wiring from the working electrode 9 to the potential control device 12 is silicone. It was pulled out of the methane fermentation tank 26a through a rubber stopper. The reference electrode 11 (silver / silver chloride electrode) was inserted into a silicone rubber stopper from the outside of the methane fermentation tank 26a and brought into contact with the fermentation broth 4. The working electrode 9, the counter electrode 10, and the reference electrode 11 were connected to a three-electrode potential controller (potentiostat) 12 to control the potential of the working electrode 9.

メタン発酵槽26aに収容される発酵液4の組成は、KH2PO4 1.135 g/l, K2HPO4 1.740 g/l, NiCl2・6H2O 0.403 mg/l, CoCl2・6H2O 0.484 mg/lとした。また、酸化還元物質としてアントラキノン-2,6-ジスルホン酸(AQDS)を終濃度0.2mMになるように添加し、メタン発酵液4の電位制御性を確保した。電解液4aの組成は、NaCl 5.844 g/lとした。 The composition of the fermented liquid 4 accommodated in the methane fermenter 26a is KH 2 PO 4 1.135 g / l, K 2 HPO 4 1.740 g / l, NiCl 2 · 6H 2 O 0.403 mg / l, CoCl 2 · 6H 2 O 0.484 mg / l. In addition, anthraquinone-2,6-disulfonic acid (AQDS) was added as a redox substance to a final concentration of 0.2 mM to ensure the potential controllability of the methane fermentation broth 4. The composition of the electrolytic solution 4a was NaCl 5.844 g / l.

発酵液4には、模擬生ゴミでメタン発酵を行って集積した種汚泥から取得した微生物群集を添加した。また、実験中は発酵液4のpHを7.4〜7.9に維持し、温度は55℃に維持した。また、発酵液4と電解液4aは攪拌子で攪拌し続けた。   To the fermentation liquid 4, a microbial community obtained from seed sludge accumulated by performing methane fermentation with simulated raw garbage was added. During the experiment, the pH of the fermentation broth 4 was maintained at 7.4 to 7.9, and the temperature was maintained at 55 ° C. Moreover, the fermented liquid 4 and the electrolyte solution 4a continued stirring with the stirring bar.

また、本参考例では、図2に示す負荷(有機物負荷量OLR、水理学的滞留時間HRT)をかけながら運転を行った。尚、メタン発酵槽の運転はフィルアンドドロー方式でおこなった。つまり一定量の発酵液を廃棄し、同量の基質を添加する方式で運転を行った。基質には、ドッグフード(日本ペットフード製)を100g/l(10重量%)、KH2PO4 1.135 g/l, K2HPO4 1.740 g/l, NiCl2・6H2O0.403 mg/l, CoCl2・6H2O0.484 mg/l含む模擬生ごみ基質を用いた。 Further, in this reference example, the operation was performed while applying the load shown in FIG. 2 (organic matter load amount OLR, hydraulic retention time HRT). The operation of the methane fermentation tank was performed by the fill and draw method. In other words, a certain amount of fermentation broth was discarded and the operation was performed by adding the same amount of substrate. The substrate, dog food (Nippon pet manufactured food) to 100 g / l (10 wt%), KH 2 PO 4 and 1.135 g / l, K 2 HPO 4 and 1.740 g / l, NiCl 2 · 6H 2 O and 0.403 mg / l, a simulated food waste substrate of CoCl 2 · 6H 2 O containing 0.484 mg / l was used.

作用電極9の電位は、参照電極11である銀・塩化銀電極電位基準で、+0.6V、+0.3V、−0.3V、−0.6Vとして、メタン発酵処理を行った。また、比較実験として、作用電極9への通電を行わずにメタン発酵処理を行った。尚、作用電極9と微生物群集を添加した発酵液4は実験開始数日前から接触させておき、予め作用電極9に若干数の微生物群集を担持させてから実験に供した。   The potential of the working electrode 9 was +0.6 V, +0.3 V, −0.3 V, and −0.6 V based on the silver / silver chloride electrode potential standard as the reference electrode 11, and the methane fermentation treatment was performed. As a comparative experiment, methane fermentation treatment was performed without energizing the working electrode 9. The fermented liquid 4 to which the working electrode 9 and the microbial community had been added was brought into contact several days before the start of the experiment, and a few microbial communities were supported on the working electrode 9 in advance before the experiment.

尚、メタン発酵液4の電位は−0.5V程度であったことから、作用電極9の電位が+0.6V、+0.3V、−0.3Vの場合には、作用電極9で酸化反応が生じており、−0.6Vでは還元反応が生じていることになる。このことは、−0.6Vでは作用電極9においてカソード電流が流れ、+0.6V、+0.3V、−0.3Vでは作用電極9にアノード電流が流れていることからも確認することができた。   Since the potential of the methane fermentation broth 4 was about −0.5 V, when the potential of the working electrode 9 was +0.6 V, +0.3 V, and −0.3 V, the oxidation reaction was performed at the working electrode 9. This occurs, and a reduction reaction occurs at -0.6V. This can be confirmed from the fact that the cathode current flows in the working electrode 9 at −0.6 V, and the anode current flows in the working electrode 9 at +0.6 V, +0.3 V, and −0.3 V. .

2.分析方法
(1)化学分析方法
メタン発酵槽26aから排出されるガスの組成(メタン、水素、二酸化炭素)は、熱伝導率検出器(GC390B、GLサイエンス製)と活性炭充填カラム(GLサイエンス製)を備えたガスクロマトグラフィーにより測定した。
2. Analysis method (1) Chemical analysis method The composition (methane, hydrogen, carbon dioxide) of the gas discharged from the methane fermentation tank 26a is a thermal conductivity detector (GC390B, manufactured by GL Science) and an activated carbon packed column (manufactured by GL Science). Was measured by gas chromatography equipped with

発酵液4の低級脂肪酸濃度分析は、分析方法:液体クロマトグラフィー(GLサイエンス製、装置名GL-7400)により行った。   The lower fatty acid concentration analysis of the fermentation broth 4 was performed by an analysis method: liquid chromatography (manufactured by GL Science, apparatus name: GL-7400).

COD(化学的酸素要求量)の分析は、分析方法:Japanese Industrial Standard (JIS) K 0102-20(HACH製、装置名DR800)により行った。   The analysis of COD (chemical oxygen demand) was performed according to the analysis method: Japanese Industrial Standard (JIS) K 0102-20 (HACH, apparatus name: DR800).

SS(浮遊固形分量)の分析は、分析方法:JIS K 0102-14.1(ヤマト製、装置名DN63)により行った。   The analysis of SS (floating solid content) was performed by an analysis method: JIS K 0102-14.1 (manufactured by Yamato, apparatus name DN63).

(2)生物学的分析方法
実験終了後に作用電極9に付着している微生物群とメタン発酵液4に含まれる微生物群の16S rRNA遺伝子のコピー数をリアルタイムPCRを用いて定量分析した。具体的には、作用電極9に付着している微生物群を懸濁させた溶液またはメタン発酵液4を遠心分離処理して微生物群を沈降させ、トリス−EDTA緩衝液 (pH8.0、100mM トリスHCl、40mM EDTA)に懸濁した。DNAはドデシル硫酸ナトリウム及びフェノール−クロロホルム−イソアミルアルコール溶液(25:24:1 v/v)の存在下、微生物群から繰り返しビーズを衝突させて抽出し、次いで、抽出DNAをQIAamp DNAミクロキット(キアゲン社製)で精製した。これを、TaqMan リアルタイムPCRに供して微生物群の16S rRNA遺伝子のコピー数を定量分析した。プライマー/プローブセットは以下の通りとした。そして、原核生物に関する定量分析結果にメタン菌に関する定量分析結果を加算して、微生物群全体の16S rRNA遺伝子のコピー数を求めた。尚、実験に使用したプライマー/プローブセットは、以下の論文に記載されているものである(Takai, K., K. Horikoshi (2000). "Rapid detection and quatification of members of archaeal community by quantitative PCR using fluorogenic probes." Appl. Environ. Microbiol. 66(11): 5066-5072.、Sawayama, S., Tsukahara K, Yagishita T (2006). "Phylogenetic description of immobilized methanogenic community using real-time PCR in a fixed-bed anaerobic digester." Bioresour. Technol. 97(1): 69-76.)。
・原核生物用プライマー/プローブセット:
Uni340F/Uni806R/Uni516F
・メタン菌用プライマー/プローブセットセット:
S-P-MArch-0348-S-a-17/S-D-Arch-0786-A-a-20/S-P-MArch-0515-S-a-25
(2) Biological analysis method The copy number of 16S rRNA gene of the microorganism group adhering to the working electrode 9 and the microorganism group contained in the methane fermentation broth 4 was quantitatively analyzed using real-time PCR. Specifically, a solution in which the microorganism group adhering to the working electrode 9 is suspended or the methane fermentation solution 4 is centrifuged to settle the microorganism group, and a Tris-EDTA buffer solution (pH 8.0, 100 mM Tris). HCl, 40 mM EDTA). DNA was extracted by repeated collision of beads from the microbial population in the presence of sodium dodecyl sulfate and phenol-chloroform-isoamyl alcohol solution (25: 24: 1 v / v), and the extracted DNA was then extracted with the QIAamp DNA micro kit (Qiagen). Purified). This was subjected to TaqMan real-time PCR to quantitatively analyze the copy number of the 16S rRNA gene of the microorganism group. The primer / probe set was as follows. And the quantitative analysis result regarding a methane bacterium was added to the quantitative analysis result regarding a prokaryote, and the copy number of 16S rRNA gene of the whole microorganism group was calculated | required. The primer / probe set used in the experiment is described in the following paper (Takai, K., K. Horikoshi (2000). "Rapid detection and quatification of members of archaeal community by quantitative PCR using fluorogenic probes. "Appl. Environ. Microbiol. 66 (11): 5066-5072., Sawayama, S., Tsukahara K, Yagishita T (2006)." Phylogenetic description of immobilized methanogenic community using real-time PCR in a fixed- bed anaerobic digester. "Bioresour. Technol. 97 (1): 69-76.).
Prokaryotic primer / probe set:
Uni340F / Uni806R / Uni516F
・ Primer / probe set for methane bacteria:
SP-MArch-0348-Sa-17 / SD-Arch-0786-Aa-20 / SP-MArch-0515-Sa-25

また、末端断片長多型解析(T−RFLP)により、全菌のうち古細菌を除く細菌の群集構造と、全菌のうち細菌を除く古細菌の群集構造とを解析した。具体的には、細菌のフォーワードプライマーとして5’末端で6-FAMでラベルされたBa27fを用い、リバースプライマーとしてBa907を用い、古細菌のフォーワードプライマーとしてAr109fを用い、リバースプライマーとして5’末端で6-FAMでラベルされたAr912rtを用いて、50μLの反応混合物中でPCRを行い、PCR単位複製配列物を得た。PCR単位複製配列物はWizard SV Gel and PCR Clean-Up System (プロメガ社製)で精製した後、細菌の制限酵素としてMspI(New England BioLabs社製)を用い、古細菌の制限酵素としてTaqI(New England BioLabs社製)を用いて消化した。この精製消化物の内部サイズ標準としてDNAサイズ標準GeneScan-500 ROX Size Standard (Applied Biosystems社製)を用いた。3130xl Genetic Analyzer(Applied Biosystems社製)により、末端断片長多型解析を実行した。尚2%未満の成分については、データから取り除いた。   Further, by analyzing the terminal fragment length polymorphism (T-RFLP), the community structure of bacteria excluding archaea out of all bacteria and the community structure of archaea excluding bacteria among all bacteria were analyzed. Specifically, Ba27f labeled with 6-FAM at the 5 'end is used as a bacterial forward primer, Ba907 is used as a reverse primer, Ar109f is used as an archaeal forward primer, and the 5' end is used as a reverse primer. PCR was performed in a 50 μL reaction mixture using Ar912rt labeled with 6-FAM in to obtain a PCR amplicon. The PCR amplicon was purified by Wizard SV Gel and PCR Clean-Up System (Promega), MspI (New England BioLabs) was used as a bacterial restriction enzyme, and TaqI (New England BioLabs) was used as an archaeal restriction enzyme. England BioLabs). The DNA size standard GeneScan-500 ROX Size Standard (Applied Biosystems) was used as an internal size standard for this purified digest. Terminal fragment length polymorphism analysis was performed using 3130xl Genetic Analyzer (Applied Biosystems). Ingredients below 2% were removed from the data.

さらに、細菌を除く古細菌について、クローン解析を行った。具体的には、T−RFLPと同様の条件でPCRを行い、PCR産物を精製してpGEM−T Easy ベクター(プロメガ社製)にライゲートさせた。プラスミドはEscherichia coli JM109細胞に組み込み、そのクローンをランダムに選択して、BigDye Terminator cycle sequencing chemistryを用いたABI 3130xl sequencer(アプライドバイオシステムズ)によりシーケンシングを行った。   Furthermore, clonal analysis was performed on archaea except bacteria. Specifically, PCR was performed under the same conditions as for T-RFLP, and the PCR product was purified and ligated into a pGEM-T Easy vector (Promega). The plasmid was incorporated into Escherichia coli JM109 cells, and clones were randomly selected and sequenced by ABI 3130xl sequencer (Applied Biosystems) using BigDye Terminator cycle sequencing chemistry.

3.実験結果
(1)設定電位とガス生成速度の関係
図3に各種設定電位におけるガス生成速度の経時変化を示す。尚、本実験で得られたガスのうち50〜70%がメタンガスであった。設定電位が+0.6Vの場合には、有機物負荷量11.2gCOD/l/日でガス生成速度が低下した(最終ガス生成速度1000ml/l/日)。また、高負荷条件下(有機物負荷量26.9gCOD/l/日)で運転を続けたところ、設定電位が−0.3Vの場合と通電なしの場合には、ガス生成速度の低下が見られた(最終ガス生成速度は共に2300ml/l/日)。一方、+0.3V及び−0.6Vの場合には、高負荷条件下(有機物負荷量26.9gCOD/l/日)で運転を続けても、ガス生成速度の低下が見られなかった(最終ガス生成速度は共に6800ml/l/日)。
3. Experimental Results (1) Relationship between Set Potential and Gas Generation Rate FIG. 3 shows changes with time in the gas generation rate at various set potentials. In addition, 50 to 70% of the gas obtained in this experiment was methane gas. When the set potential was +0.6 V, the gas generation rate decreased at an organic load of 11.2 g COD / l / day (final gas generation rate of 1000 ml / l / day). In addition, when the operation was continued under high load conditions (organic matter load: 26.9 g COD / l / day), a decrease in gas generation rate was observed when the set potential was -0.3 V and when there was no energization. (Final gas production rate is 2300 ml / l / day). On the other hand, in the case of + 0.3V and -0.6V, even if the operation was continued under a high load condition (organic matter load 26.9 g COD / l / day), no decrease in gas generation rate was observed (final) (The gas generation rate is 6800 ml / l / day for both).

(2)設定電位とCOD除去速度の関係
図4に各種設定電位におけるCOD除去速度の経時変化を示す。設定電位が+0.6Vの場合には、COD除去速度の有機物負荷量の増加に伴う上昇は見られなかった(最終COD除去速度3.1gCOD/l/日)。また、設定電位が−0.3V、通電なし、+0.3V、−0.6Vの場合にはそれぞれCOD除去速度の有機物負荷量の増加に伴う上昇が見られ、有機物負荷量が26.9gCOD/l/日に上昇した場合にもCOD除去速度は上昇した。特に、設定電位が−0.6Vと+0.3Vの場合にCOD除去速度の上昇が顕著であった。尚、最終的なCOD除去速度は16.1gCOD/l/日(設定電位−0.6V)、12.0gCOD/l/日(通電なし)、12.6gCOD/l/日(設定電位−0.3V)、15.4gCOD/l/日(設定電位+0.3V)であった。
(2) Relationship between set potential and COD removal rate FIG. 4 shows changes with time in the COD removal rate at various set potentials. When the set potential was +0.6 V, the COD removal rate did not increase with the increase in the organic load (final COD removal rate 3.1 g COD / l / day). Further, when the set potential is −0.3 V, no energization, +0.3 V, and −0.6 V, the COD removal rate increases with an increase in the organic load, and the organic load is 26.9 g COD / The COD removal rate also increased when increased to 1 / day. In particular, the increase in the COD removal rate was significant when the set potential was −0.6 V and +0.3 V. The final COD removal rates were 16.1 g COD / l / day (set potential −0.6 V), 12.0 g COD / l / day (no energization), 12.6 g COD / l / day (set potential −0.1 V). 3V), 15.4 g COD / l / day (set potential +0.3 V).

(3)設定電位とSS除去速度の関係
図5に各種設定電位におけるSS除去速度の経時変化を示す。設定電位が+0.3V、−0.6Vの場合には、有機物負荷量の増加に伴い、SS除去速度も上昇する傾向が見られ、有機物負荷量が26.9gCOD/l/日に上昇した場合にもSS除去速度の上昇が見られた。尚、最終的なSS除去速度は、4.8g/l/日(設定電位−0.6V)、5.0g/l/日(設定電位+0.3V)であった。また、設定電位が−0.3V、通電なしの場合には、有機物負荷量の増加に伴うSS除去速度の大幅な上昇は見られなかった。尚、最終的なSS除去速度は、3.3g/l/日(設定電位−0.3V)、3.0g/l/日(通電なし)であった。
(3) Relationship between set potential and SS removal rate FIG. 5 shows changes with time in the SS removal rate at various set potentials. When the set potential is +0.3 V or -0.6 V, the SS removal rate tends to increase as the organic load increases, and the organic load increases 26.9 g COD / l / day. Also, an increase in the SS removal rate was observed. The final SS removal rates were 4.8 g / l / day (set potential −0.6 V) and 5.0 g / l / day (set potential +0.3 V). In addition, when the set potential was −0.3 V and no current was supplied, no significant increase in the SS removal rate accompanying an increase in the organic load was observed. The final SS removal rate was 3.3 g / l / day (set potential −0.3 V) and 3.0 g / l / day (no power supply).

(4)設定電位と低級脂肪酸濃度の関係
図6に各種設定電位における低級脂肪酸濃度(酢酸、酪酸、プロピオン酸)の経時変化を示す。設定電位が+0.6Vの場合には、20日目あたりで既に低級脂肪酸の蓄積が見られた。また、(有機物負荷量26.9gCOD/l/日)で運転を続けたところ、設定電位が−0.3Vの場合と通電なしの場合には、低級脂肪酸の蓄積が見られた。一方で、設定電位が+0.3Vと−0.6Vの場合には、低級脂肪酸の蓄積が見られなかった。この結果から、設定電位を+0.3Vと−0.6Vにした場合には、メタン発酵槽の酸敗を防いで、長期にわたりメタン発酵処理を実施できることが明らかとなった。
(4) Relationship between set potential and lower fatty acid concentration FIG. 6 shows changes with time in lower fatty acid concentrations (acetic acid, butyric acid, propionic acid) at various set potentials. When the set potential was +0.6 V, accumulation of lower fatty acids was already observed around the 20th day. Further, when the operation was continued at (organic substance loading 26.9 g COD / l / day), accumulation of lower fatty acids was observed when the set potential was −0.3 V and when no current was supplied. On the other hand, when the set potential was +0.3 V and −0.6 V, accumulation of lower fatty acids was not observed. From this result, it was clarified that when the set potential was set to +0.3 V and −0.6 V, the methane fermentation treatment can be performed over a long period of time by preventing the methane fermentation tank from being spoiled.

(参考例A−2)
上記参考例A−1の実験が終了した後、発酵液画分と担体付着画分とを遺伝子学的解析に供し、微生物の付着状態と微生物群の分布状態について検討した。
(Reference Example A-2)
After the experiment of Reference Example A-1 was completed, the fermented liquid fraction and the carrier-adhered fraction were subjected to genetic analysis, and the state of microbial adhesion and the state of microbial population distribution were examined.

1.全菌とメタン菌の定量PCR結果
参考例A−1の実験終了後、発酵液の画分と担体付着画分とを取得し、全菌及びメタン菌のコピー数を定量PCRにより測定した。結果を図7〜10に示す。図7が発酵液画分の全菌のコピー数であり、図8が発酵液画分のメタン菌のコピー数であり、図9が担体付着画分の全菌のコピー数であり、図10が担体付着画分のメタン菌のコピー数である。この結果、いずれの画分においても、設定電位が+0.3Vと−0.6Vの場合には、通電なしの場合と比較してコピー数が大幅に増加することが明らかとなった。また、発酵液画分については、通電なしの場合と設定電位が+0.3Vと−0.6Vの場合でコピー数が2〜5倍程度しか変わらなかったにも関わらず、担体付着画分については、通電なしの場合と設定電位が+0.3Vと−0.6Vの場合でコピー数が400〜900倍も変わることが明らかとなった。このことから、参考例A−1において見られた高負荷条件におけるメタン発酵処理能の維持ないしは向上効果は、担体付着画分が大幅に増加することに起因することが明らかとなった。
1. Quantitative PCR Results for Whole Bacteria and Methane Bacteria After completion of the experiment in Reference Example A-1, a fraction of the fermentation broth and a carrier-attached fraction were obtained, and the copy numbers of the whole bacteria and methane bacteria were measured by quantitative PCR. The results are shown in FIGS. FIG. 7 shows the copy number of all the bacteria in the fermentation broth fraction, FIG. 8 shows the copy number of methane bacteria in the fermented liquid fraction, FIG. 9 shows the copy number of all bacteria in the carrier-attached fraction, and FIG. Is the copy number of methane bacteria in the carrier-attached fraction. As a result, it has been clarified that in any fraction, when the set potential is +0.3 V and −0.6 V, the number of copies is greatly increased as compared with the case where no power is supplied. In addition, as for the fermented liquor fraction, the carrier-adhered fraction was not changed in the case of no energization and the set potential was +0.3 V and -0.6 V, although the copy number changed only about 2 to 5 times. It has been clarified that the copy number varies by 400 to 900 times between the case of no energization and the case where the set potential is + 0.3V and −0.6V. From this, it was clarified that the maintenance or improvement effect of the methane fermentation treatment performance under the high load condition seen in Reference Example A-1 is caused by a significant increase in the fraction adhered to the carrier.

2.T−RFLPによる細菌群集構造の比較
末端断片長多型解析(T−RFLP)により、全菌のうち、古細菌を除く細菌の群集構造を比較した。結果を図11に示す。図11に示される結果から、設定電位が+0.3Vと−0.6Vの場合に、262bpに該当する微生物の占める割合が大きくなり、特に炭素板においてその傾向が顕著であった。尚、図11中のかっこ内の電位は、発酵液の電位を意味している。つまり、作用電極9(担体)の電位と、発酵液の電位は異なるものである。
2. Comparison of bacterial community structure by T-RFLP By end fragment length polymorphism analysis (T-RFLP), the bacterial community structure of all bacteria except archaea was compared. The results are shown in FIG. From the results shown in FIG. 11, when the set potential was +0.3 V and −0.6 V, the proportion of microorganisms corresponding to 262 bp increased, and this tendency was particularly remarkable in the carbon plate. In addition, the electric potential in the parenthesis in FIG. 11 means the electric potential of the fermentation broth. That is, the potential of the working electrode 9 (carrier) and the potential of the fermentation broth are different.

次に、TAクローニングにより細菌群集の構造を解析した結果を図12に示す。この解析結果から、262bpに該当する微生物が、サーモトガ(Thermotogae)門に属する微生物であることが明らかとなった。したがって、サーモトガ(Thermotogae)門に属する微生物がSS除去及びCOD除去において、有効に作用していることが考えられた。また、このことから、サーモトガ(Thermotogae)門に属する微生物を含む微生物群集を培養液に添加し、培養液と微生物を担持し得る導電性担体、例えば炭素製の担体を接触させて、導電性担体の電位を銀・塩化銀電極電位基準で−0.6Vまたは+0.3Vに設定することで、サーモトガ(Thermotogae)門に属する微生物を導電性担体上に担持させて活性化させることができ、SS除去及びCOD除去を高負荷環境下においても効率よく実施できることが明らかとなった。   Next, the result of analyzing the structure of the bacterial community by TA cloning is shown in FIG. From this analysis result, it was revealed that a microorganism corresponding to 262 bp is a microorganism belonging to the Thermotogae gate. Therefore, it was considered that microorganisms belonging to the Thermotogae gate acted effectively in SS removal and COD removal. In addition, from this, a microbial community containing microorganisms belonging to Thermotogae is added to the culture solution, and the culture solution and a conductive carrier capable of supporting the microorganisms, for example, a carbon carrier, are brought into contact with each other. Is set to -0.6V or + 0.3V on the basis of the silver / silver chloride electrode potential, microorganisms belonging to Thermotogae can be supported on the conductive support and activated, and SS It was revealed that removal and COD removal can be carried out efficiently even under a high load environment.

また、図11に示される結果から、設定電位が+0.3Vと−0.6Vの場合に、210bpに該当する微生物が検出されなくなったことから、210bpに該当する微生物がSS除去及びCOD除去の阻害要因となっており、設定電位を+0.3Vと−0.6Vとすることで、210bpに該当する微生物を失活または除去して、SS除去及びCOD除去を高負荷環境下においても効率よく実施できる効果が得られる可能性もこの実験から示唆された。   In addition, from the results shown in FIG. 11, when the set potential is +0.3 V and −0.6 V, the microorganisms corresponding to 210 bp are not detected, and thus the microorganisms corresponding to 210 bp are subjected to SS removal and COD removal. It is an inhibiting factor, and by setting the set potential to +0.3 V and -0.6 V, microorganisms corresponding to 210 bp are inactivated or removed, and SS removal and COD removal are efficiently performed even in a high load environment. This experiment also suggested the possibility of obtaining a practicable effect.

さらに、サーモトガ(Thermotogae)門に属する微生物が低級脂肪酸の分解に関与しており、設定電位を+0.3Vと−0.6Vとすることで、低級脂肪酸の分解を促進できる可能性も示唆された。また、210bpに該当する微生物が低級脂肪酸の蓄積を促進しており、設定電位を+0.3Vと−0.6Vとすることで、低級脂肪酸の蓄積を抑えられる可能性も示唆された。   Furthermore, it was suggested that microorganisms belonging to the Thermotogae gate are involved in the degradation of lower fatty acids, and that the degradation of lower fatty acids can be promoted by setting the set potential to +0.3 V and -0.6 V. . In addition, it was suggested that microorganisms corresponding to 210 bp promote accumulation of lower fatty acids, and that the accumulation of lower fatty acids can be suppressed by setting the set potential to +0.3 V and −0.6 V.

そして、さらに解析を進めた結果、設定電位が−0.6Vの場合に炭素板に付着していた95bp微生物が蛋白質分解能を有すると考えられるBacteroidetes門の細菌に近縁性を示し、150bpの細菌は生ごみの蛋白質や繊維分を特異的に分解していると考えられているFirmicutes門の細菌に近縁性を示すことが確認された。このことから、設定電位を−0.6Vとすることで、有機性廃棄物のメタン発酵処理に有効な微生物群を担体に付着させる効果があることも明らかとなった。 The result of further analysis, shows a relatedness to bacterial Bacteroidetes Gate microorganisms 95bp adhering to the carbon plate is considered to have a protein resolution when setting potential of -0.6 V, the 150bp It was confirmed that the bacteria are closely related to the bacteria of the Firmicutes, which are thought to specifically degrade food proteins and fiber. From this, it was also clarified that setting the set potential to −0.6 V has an effect of attaching a microorganism group effective for methane fermentation treatment of organic waste to the carrier.

3.T−RFLPによる古細菌群集構造の比較
末端断片長多型解析(T−RFLP)により、全菌のうち、細菌を除く古細菌の群集構造を比較した。尚、古細菌にはメタン生成菌が含まれている。結果を図13に示す。設定電位が+0.3Vの場合には、92bpに該当する微生物の占める割合が大きくなり、特に炭素板においてその傾向が顕著であったが、186bpに該当する微生物については占有割合が殆ど変わらなかった。設定電位が−0.6Vの場合には、炭素板において186bpに該当する微生物の占有割合の若干の増加と、92bpに該当する微生物の占有割合の若干の増加が見られた。
3. Comparison of archaeal community structure by T-RFLP Comparison of archaea community structure excluding bacteria among all bacteria by end fragment length polymorphism analysis (T-RFLP). The archaebacteria contain methanogens. The results are shown in FIG. When the set potential was +0.3 V, the proportion of microorganisms corresponding to 92 bp increased, and the tendency was particularly remarkable in the carbon plate, but the proportion of microorganisms corresponding to 186 bp remained almost unchanged. . When the set potential was −0.6 V, a slight increase in the occupation ratio of microorganisms corresponding to 186 bp and a slight increase in the occupation ratio of microorganisms corresponding to 92 bp were observed on the carbon plate.

次に、TAクローニングにより古細菌群集の構造を解析した結果を図14に示す。この結果から、設定電位が+0.3Vの場合に占有割合が増加した92bpに該当する微生物が水素資化性メタン生成菌であるMethanothermobacter thermautotrophicusであることが明らかとなった。また、186bpに該当する微生物が酢酸資化性メタン生成菌であるMethanosarcina thermophilaであり、設定電位が+0.3V及び−0.6Vの場合には、その占有割合が通電なしの場合と同等かあるいは若干増加しており、低級脂肪酸である酢酸の蓄積の抑制につながったものと考えられた。つまり、定量PCRの結果から、設定電位が+0.3V及び−0.6Vの場合には、通電なしの場合と比較して担体上でメタン生成菌のコピー数の大幅な増加が確認されていることから、メタン生成菌の増殖に伴って酢酸資化性メタン生成菌もその占有割合を維持しながら増加しており、その結果として低級脂肪酸である酢酸の蓄積の抑制につながったものと考えられた。   Next, the results of analyzing the structure of the archaeal community by TA cloning are shown in FIG. From this result, it was clarified that the microorganism corresponding to 92 bp whose occupation ratio increased when the set potential was +0.3 V was Methanothermobacter thermautotrophicus, which is a hydrogen-assimilating methanogen. In addition, when the microorganism corresponding to 186 bp is Methanosarcina thermophila which is an acetic acid-assimilating methanogen and the set potential is +0.3 V and −0.6 V, the occupation ratio is the same as when no current is supplied or It was thought that this increased slightly, leading to the suppression of acetic acid accumulation, which is a lower fatty acid. That is, from the results of quantitative PCR, when the set potential is +0.3 V and −0.6 V, it is confirmed that the copy number of methanogenic bacteria on the carrier is significantly increased as compared with the case where no current is supplied. Therefore, acetic acid-assimilating methanogens increased with the growth of methanogens while maintaining their occupation ratio, and as a result, the accumulation of acetic acid, which is a lower fatty acid, was thought to have been suppressed. It was.

以上の結果から、酢酸資化性メタン生成菌であるMethanosarcina thermophilaを含む微生物群集を培養液に添加し、培養液と微生物を担持し得る導電性担体、例えば炭素製の担体を接触させて、導電性担体の電位を銀・塩化銀電極電位基準で−0.6Vまたは+0.3Vに設定することで、酢酸を生成源としてメタンガスを効率よく生成できることが明らかとなった。   Based on the above results, a microbial community containing Methanosarcina thermophila, which is an acetic acid-assimilating methanogen, is added to the culture solution, and a conductive carrier that can support the microorganism, for example, a carbon carrier, is brought into contact with the culture solution. It has been clarified that methane gas can be efficiently generated using acetic acid as a generation source by setting the potential of the active carrier to −0.6 V or +0.3 V based on the silver / silver chloride electrode potential.

また、水素資化性メタン生成菌であるMethanothermobacter thermautotrophicusを含む微生物群集を培養液に添加し、培養液と微生物を担持し得る導電性担体、例えば炭素製の担体を接触させて、導電性担体の電位を銀・塩化銀電極電位基準で−0.6Vまたは+0.3Vに設定することで、水素ガスと二酸化炭素を生成源としてメタンガスを効率よく生成できることが明らかとなった。   In addition, a microbial community containing Methanothermobacter thermautotrophicus, which is a hydrogen-utilizing methanogen, is added to the culture solution, and the culture solution is contacted with a conductive carrier that can support the microorganism, for example, a carbon carrier. It has been clarified that methane gas can be efficiently generated using hydrogen gas and carbon dioxide as a generation source by setting the potential to -0.6 V or +0.3 V on the basis of the silver / silver chloride electrode potential.

(参考例A−3)
水素資化性メタン生成菌であるMethanothermobacter thermautotrophicusについて、菌体自体の活性を設定電位により高めて、メタン生成速度を増加させることが可能か検討した。
(Reference Example A-3)
We investigated whether Methanothermobacter thermautotrophicus, a hydrogen-utilizing methanogen, could increase the methane production rate by increasing the activity of the cell itself with a set potential.

図17に示す実験装置を用いて実験を行った。250mL容のガラスバイアル瓶(Duran製)を培養容器5とし、培養液4の液面より下部に開口部を3つ設けた。1つめの開口部5bには参照電極11(東亜DDK製、HS−205C、銀・塩化銀電極)を差し込んで参照電極11と培養液4とを接触させた。2つめの開口部5cは培養液4を採取するために設け、蓋の開閉により培養液4を採取可能とした。3つめの開口部5aはポーラス板状の炭素電極(対電極10)で塞ぎ、この板状の炭素電極の片側表面の下半分には20%ナフィオン分散液(DE2021)を塗布し、さらにナフィオン膜N117で覆うことでイオン交換膜6を形成し、イオン交換膜6によって3つめの開口部5aが塞がれるようにした。対電極10をポーラスなものとした理由は、イオン交換膜6と対電極10との接触面で発生したガスを対電極10の反対側の面に通過しやすくするためである。作用電極9(導電性担体)として板状の炭素電極を培養液4に浸した。作用電極9と対電極10と参照電極11とを3電極式の電位制御装置(ポテンシオスタット)12に結線して、作用電極9(導電性担体)の電位を厳密に制御可能とした。尚、培養液4は培養容器5の8分目程度まで入れ、液面上部にヘッドスペースを確保した。培養容器5には蓋18をし、蓋18の上面18aに弾性材料であるシリコーンゴムを備えて、注射器の注射針を差し込んで培養容器5内のヘッドスペースからガス状物質を回収可能とし、且つ注射針の差し込みにより生じた孔が注射針を抜いた際に塞がるようにした。   Experiments were performed using the experimental apparatus shown in FIG. A 250 mL glass vial (manufactured by Duran) was used as the culture container 5, and three openings were provided below the liquid level of the culture solution 4. The reference electrode 11 (manufactured by Toa DDK, HS-205C, silver / silver chloride electrode) was inserted into the first opening 5b, and the reference electrode 11 and the culture solution 4 were brought into contact with each other. The second opening 5c is provided to collect the culture solution 4, and the culture solution 4 can be collected by opening and closing the lid. The third opening 5a is closed with a porous plate-like carbon electrode (counter electrode 10), and 20% Nafion dispersion (DE2021) is applied to the lower half of the surface of one side of this plate-like carbon electrode. The ion exchange membrane 6 was formed by covering with N117, and the third opening 5a was blocked by the ion exchange membrane 6. The reason why the counter electrode 10 is made porous is that gas generated at the contact surface between the ion exchange membrane 6 and the counter electrode 10 can easily pass through the opposite surface of the counter electrode 10. A plate-like carbon electrode was immersed in the culture solution 4 as the working electrode 9 (conductive carrier). The working electrode 9, the counter electrode 10, and the reference electrode 11 were connected to a three-electrode potential control device (potentiostat) 12 so that the potential of the working electrode 9 (conductive carrier) could be strictly controlled. In addition, the culture solution 4 was put into the culture vessel 5 until about the eighth minute, and a head space was secured above the liquid level. The culture container 5 is provided with a lid 18, and an upper surface 18 a of the lid 18 is provided with a silicone rubber that is an elastic material. The syringe needle of the syringe can be inserted to collect a gaseous substance from the head space in the culture container 5, and The hole produced by inserting the injection needle was closed when the injection needle was removed.

培養温度は55℃とした。また、培養液4にAQDS(アントラキノン−2,6−ジスルホン酸)を添加し、AQDS濃度は0.5mMとした。尚、培養液4は攪拌子19で攪拌し、上部のシリコーンゴム栓に注射針を2本刺し、一方の注射針からH/CO=80/20混合ガスを1時間通気することにより、ヘッドスペースをHとCOの混合ガスで置換した。培養液4の組成は以下の通りとした。また、培養液4のpHは7.2とした。
<培養液組成(/L)>KH2PO4 0.3 g, (NH4)2SO4 1.5 g, NaCl 0.6 g, MgSO4・7H2O 0.12 g, CaCl2・2H2O 0.08 g, FeSO4・7H2O 4.0 mg, K2HPO4 0.15 g, Na2CO3 4.0 g, Trace vitamins 10.0 ml, Trace element solution 10.0 ml, L-Cysteine・HCl・H2O 0.5 g, Na2S・9H2O 0.5 g, Resazurin 1.0 mg
<Vitamin solution(/L)>Biotin 2.0 mg, Folic acid 2.0 mg, Pyridoxine-HCl 10.0 mg, Thiamine-HCl・2H2O 5.0 mg, Riboflavine 5.0 mg, Nicotinic acid 5.0 mg, Ca-pantothenate 5.0 mg, p-Aminobenzoic acid 1.0 mg, Vitamin B12 0.01 mg
<Trace element solution(/L)>Na2・EDTA 0.64 g, MgSO4・7H2O 6.2 g, MnSO4・4H2O 0.55 g, NaCl 1.0 g, FeSO4・7H2O 0.1 g, CoCl2・6H2O 0.17 g, CaCl2・2H2O 0.13 g, ZnSO4・7H2O 0.18 g, CuSO4 0.05 g, KAl(SO4)2・12H2O 0.018 g, H3BO3 0.01 g, Na2MoO4・12H2O 0.011 g, NiCl2・6H2O 0.025 g
The culture temperature was 55 ° C. Further, AQDS (anthraquinone-2,6-disulfonic acid) was added to the culture solution 4 so that the AQDS concentration was 0.5 mM. The culture solution 4 is stirred with a stir bar 19, two injection needles are inserted into the upper silicone rubber stopper, and H 2 / CO 2 = 80/20 mixed gas is aerated from one injection needle for 1 hour. The head space was replaced with a mixed gas of H 2 and CO 2 . The composition of the culture solution 4 was as follows. The pH of the culture solution 4 was 7.2.
<Culture solution composition (/ L)> KH 2 PO 4 0.3 g, (NH 4 ) 2 SO 4 1.5 g, NaCl 0.6 g, MgSO 4 .7H 2 O 0.12 g, CaCl 2 .2H 2 O 0.08 g, FeSO 4・ 7H 2 O 4.0 mg, K 2 HPO 4 0.15 g, Na 2 CO 3 4.0 g, Trace vitamins 10.0 ml, Trace element solution 10.0 ml, L-Cysteine ・ HCl ・ H2O 0.5 g, Na 2 S ・ 9H 2 O 0.5 g, Resazurin 1.0 mg
<Vitamin solution (/ L)> Biotin 2.0 mg, Folic acid 2.0 mg, Pyridoxine-HCl 10.0 mg, Thiamine-HCl · 2H 2 O 5.0 mg, Riboflavine 5.0 mg, Nicotinic acid 5.0 mg, Ca-pantothenate 5.0 mg, p- Aminobenzoic acid 1.0 mg, Vitamin B 12 0.01 mg
<Trace element solution (/ L)> Na 2 · EDTA 0.64 g, MgSO 4 · 7H 2 O 6.2 g, MnSO 4 · 4H 2 O 0.55 g, NaCl 1.0 g, FeSO 4 · 7H 2 O 0.1 g, CoCl 2 · 6H 2 O 0.17 g, CaCl 2・ 2H 2 O 0.13 g, ZnSO 4・ 7H 2 O 0.18 g, CuSO 4 0.05 g, KAl (SO 4 ) 2・ 12H 2 O 0.018 g, H 3 BO 3 0.01 g, Na 2 MoO 4・ 12H 2 O 0.011 g, NiCl 2・ 6H 2 O 0.025 g

結果を図15に示す。尚、図15の相対活性とは、通電しない条件での菌体当たりのメタン生成量を1とした相対評価値である。即ち、この値を比較することで、メタン生成菌1菌体当たりのメタン生成活性を評価することができる。   The results are shown in FIG. Note that the relative activity in FIG. 15 is a relative evaluation value where the amount of methane produced per cell under the condition where no current is supplied is 1. That is, by comparing these values, the methanogenic activity per methanogenic cell can be evaluated.

図15に示される結果から、作用電極9(導電性担体)の設定電位を−0.8Vとすることで、通電しない場合と比較してメタン生成活性が3.5倍向上することが明らかとなった。   From the results shown in FIG. 15, it is clear that setting the working potential of the working electrode 9 (conductive carrier) to −0.8 V improves the methane production activity by 3.5 times compared to the case where no current is supplied. became.

この実験結果から、導電性担体の電位を−0.6Vまたは+0.3Vに制御して担体に水素資化性メタン生成菌であるMethanothermobacter thermautotrophicusを優占的に担持させた後、導電性担体の電位を−0.8Vに制御することで、極めて高効率にメタンを生成できることが明らかとなった。   From this experimental result, the potential of the conductive carrier is controlled to −0.6 V or +0.3 V, and the carrier is preferentially loaded with Methanothermobacter thermautotrophicus which is a hydrogen-assimilating methanogen. It was revealed that methane can be generated with extremely high efficiency by controlling the potential to -0.8V.

(参考例A−4)
担体付着画分の菌数よりも発酵液画分の菌数を多くして、ガス生成速度の検証を行った。
(Reference Example A-4)
The number of bacteria in the fermented liquid fraction was increased from the number of bacteria in the carrier-attached fraction, and the gas production rate was verified.

実験は以下の9条件の担体を発酵液に浸して実施した。尚、発酵液は、模擬生ゴミでメタン発酵を行って集積した種汚泥を脱イオン水で1/3に希釈して200ml使用した。
(a)PE:ポリエチレン製の担体
(b)C:炭素製の担体
(c)PP:ポリプロピレン製の担体
(d)PE+Bf:ポリエチレン製の担体にバイオフィルムを付着
(e)C+Bf:炭素製の担体にバイオフィルムを付着
(f)PP+Bf:ポリプロピレン製の担体にバイオフィルムを付着
(g)担体なし
The experiment was performed by immersing a carrier under the following nine conditions in the fermentation broth. In addition, 200 ml of the fermented liquor was used by diluting seed sludge accumulated by performing methane fermentation with simulated raw garbage to 1/3 with deionized water.
(A) PE: polyethylene carrier (b) C: carbon carrier (c) PP: polypropylene carrier (d) PE + Bf : biofilm attached to polyethylene carrier (e) C + Bf : carbon (F) PP + Bf : Adhering biofilm to polypropylene carrier (g) No carrier

運転条件は、0.95g/l/日とした。尚、(d)〜(f)のバイオフィルムを付着した条件においても、担体担持画分と比較して発酵液画分の方が菌数が多い。   The operating conditions were 0.95 g / l / day. In addition, even under the conditions where the biofilms (d) to (f) are attached, the fermentation liquid fraction has more bacteria than the carrier-supported fraction.

結果を図16に示す。(d)〜(f)の条件については、ガス生成速度が徐々に増加する傾向が見られたが、その他の条件については、ガス生成速度の増加が殆ど見られなかった。この結果から、担体に付着している菌は活性が高く、スタートアップに寄与したものと考えられた。   The results are shown in FIG. Regarding the conditions (d) to (f), there was a tendency for the gas generation rate to gradually increase, but for other conditions, there was almost no increase in the gas generation rate. From these results, it was considered that the bacteria attached to the carrier had high activity and contributed to start-up.

以上の結果から、担体付着画分を増加させることで、微生物反応プロセスの進行に極めて有利に作用することが明らかとなった。このことから、本発明のように導電性担体の電位を制御して目的の微生物群を予め担持・集積させ、あるいは処理を行いながら担持・集積させることによって、極めて効率よく微生物反応プロセスを進行させて所望の処理を実施できることが明らかとなった。   From the above results, it became clear that increasing the fraction adhered to the carrier has a very advantageous effect on the progress of the microbial reaction process. Therefore, as in the present invention, by controlling the potential of the conductive carrier and supporting and accumulating the target microorganism group in advance, or by supporting and accumulating while performing the treatment, the microbial reaction process can proceed extremely efficiently. It has become clear that the desired treatment can be carried out.

(参考例B−1)
1.実験装置及び実験方法
参考例A−1と同様の実験装置及び実験方法により、設定電位を変更して実験を実施した。また、参考例A−1において実施された一部の設定電位条件での実験について、再度実験を行い、再現性を確認した。
(Reference Example B-1)
1. Experimental Apparatus and Experimental Method An experiment was performed by changing the set potential using the same experimental apparatus and experimental method as in Reference Example A-1. Moreover, about the experiment on the one part set potential conditions implemented in Reference example A-1, it experimented again and confirmed reproducibility.

具体的には、作用電極9の電位を、参照電極11である銀・塩化銀電極電位基準で+0.0V、−0.8Vとした条件で新たに実験を実施した。−0.8Vでの実験は3回実施した。   Specifically, an experiment was newly conducted under the condition that the potential of the working electrode 9 was +0.0 V and −0.8 V based on the potential of the silver / silver chloride electrode as the reference electrode 11. The experiment at −0.8 V was performed three times.

また、通電無しの条件と−0.6Vの条件について、参考例A−1で得られた結果の再現性を確認する実験を2回実施した。   Moreover, the experiment which confirms the reproducibility of the result obtained by reference example A-1 about the conditions without electricity supply and the condition of -0.6V was implemented twice.

さらに、−0.6Vの条件と−0.8Vの条件について、有機物負荷量(OLR)を増大させて実験を行った。−0.6Vの条件については、本参考例で行った2回の実験とも、有機物負荷量を31.8g/l/日まで増加させた。−0.8Vの条件については、本参考例で行った3回の実験のうちの2回の実験について、有機物負荷量を31.8g/l/日まで増加させた。本参考例におけるメタン発酵槽の運転条件(負荷条件)を図18に示す。   Furthermore, an experiment was performed by increasing the organic load (OLR) under the conditions of -0.6V and -0.8V. Regarding the condition of −0.6 V, the organic load was increased to 31.8 g / l / day in the two experiments performed in this reference example. With respect to the condition of −0.8 V, the organic load was increased to 31.8 g / l / day for two of the three experiments performed in this reference example. The operation conditions (load conditions) of the methane fermenter in this reference example are shown in FIG.

尚、−0.6V、−0.8Vでは作用電極9上で還元反応が生じていることになる。このことは、−0.6V、−0.8Vでは作用電極9においてカソード電流が流れていることからも確認することができた。   Incidentally, at -0.6 V and -0.8 V, a reduction reaction occurs on the working electrode 9. This could be confirmed from the fact that the cathode current flows in the working electrode 9 at −0.6V and −0.8V.

2.実験結果
(1)設定電位とガス生成速度の関係
図19に各種設定電位におけるガス生成速度の経時変化を示す。図19において、×は通電無しの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)をそのままプロットしたものである。○は−0.8Vの条件の3回の実験結果の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。□は−0.6Vの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。△は+0.0Vの条件の実験結果である。◇(−0.3V)、◆(+0.3V)及び▲(+0.6V)で示される実験結果は、参考例A−1で得られた結果をそのまま掲載したものである。
2. Experimental Results (1) Relationship between Set Potential and Gas Generation Rate FIG. 19 shows changes over time in gas generation rate at various set potentials. In FIG. 19, x is a plot of three experimental results (one experimental result in Reference Example A-1 and two experimental results in the present Reference Example) under no-energization conditions. ○ is a plot of the average of three experimental results under the condition of -0.8 V. For data before increasing the organic load to 31.8 g / l / day, the standard deviation is the error bar. It showed in. □ is a plot of average values of three experimental results under the condition of −0.6 V (one experimental result in Reference Example A-1 and two experimental results in this Reference Example), and the organic load For data up to 31.8 g / l / day before increasing, the standard deviation is indicated by error bars. Δ is the experimental result under the condition of + 0.0V. The experimental results indicated by ◇ (−0.3V), ♦ (+ 0.3V) and ▲ (+ 0.6V) are the results obtained in Reference Example A-1 as they are.

通電無しの条件と−0.6Vの条件については、参考例A−1と同様の傾向が確認された。また、+0.3V及び−0.6Vの条件に加えて、−0.8Vの条件についても、運転期間中にガス生成速度の低下が見られなかった。特に、−0.6V及び−0.8Vの条件については、有機物負荷量を31.8g/l/日まで増加させても、ガス生成速度の低下は見られなかった。   About the conditions without electricity supply and the conditions of -0.6V, the tendency similar to reference example A-1 was confirmed. In addition to the conditions of +0.3 V and -0.6 V, no decrease in gas generation rate was observed during the operation period under the condition of -0.8 V. In particular, under the conditions of -0.6 V and -0.8 V, no decrease in gas generation rate was observed even when the organic load was increased to 31.8 g / l / day.

(2)設定電位とCOD除去速度の関係
図20に各種設定電位におけるCOD除去速度の経時変化を示す。図20において、×は通電無しの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)の平均値をプロットしたものであり、標準偏差をエラーバーで示した。○は−0.8Vの条件の3回の実験結果の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。□は−0.6Vの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。△は+0.0Vの条件の実験結果である。◇(−0.3V)、◆(+0.3V)及び▲(+0.6V)で示される実験結果は、参考例A−1で得られた結果をそのまま掲載したものである。
(2) Relationship between set potential and COD removal rate FIG. 20 shows changes over time in the COD removal rate at various set potentials. In FIG. 20, x is a plot of average values of three experimental results (one experimental result in Reference Example A-1 and two experimental results in the present Reference Example) under the condition of no energization. Deviations are indicated by error bars. ○ is a plot of the average of three experimental results under the condition of -0.8 V. For data before increasing the organic load to 31.8 g / l / day, the standard deviation is the error bar. It showed in. □ is a plot of average values of three experimental results under the condition of −0.6 V (one experimental result in Reference Example A-1 and two experimental results in this Reference Example), and the organic load For data up to 31.8 g / l / day before increasing, the standard deviation is indicated by error bars. Δ is the experimental result under the condition of + 0.0V. The experimental results indicated by ◇ (−0.3V), ♦ (+ 0.3V) and ▲ (+ 0.6V) are the results obtained in Reference Example A-1 as they are.

通電無しの条件と−0.6Vの条件については、参考例A−1と同様の傾向が確認された。また、+0.3V及び−0.6Vの条件に加えて、−0.8Vの条件についても、有機物負荷量の増加に伴い、COD除去速度が低下することなく上昇し続けた。特に、−0.6V及び−0.8Vの条件については、有機物負荷量を31.8g/l/日まで増加させても、COD除去速度は低下することなく上昇し続けた。   About the conditions without electricity supply and the conditions of -0.6V, the tendency similar to reference example A-1 was confirmed. Further, in addition to the conditions of +0.3 V and -0.6 V, the condition of -0.8 V continued to increase without decreasing the COD removal rate with the increase in the organic load. In particular, for the conditions of −0.6 V and −0.8 V, the COD removal rate continued to increase without decreasing even when the organic load was increased to 31.8 g / l / day.

(3)設定電位とSS除去速度の関係
図21に各種設定電位におけるSS除去速度の経時変化を示す。図21において、×は通電無しの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)の平均値をプロットしたものであり、標準偏差をエラーバーで示した。○は−0.8Vの条件の3回の実験結果の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。□は−0.6Vの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。△は+0.0Vの条件の実験結果である。◇(−0.3V)及び◆(+0.3V)で示される実験結果は、参考例A−1で得られた結果をそのまま掲載したものである。
(3) Relationship between set potential and SS removal rate FIG. 21 shows changes with time in the SS removal rate at various set potentials. In FIG. 21, x is a plot of average values of three experimental results (one experimental result in Reference Example A-1 and two experimental results in the present Reference Example) under the condition of no energization. Deviations are indicated by error bars. ○ is a plot of the average of three experimental results under the condition of -0.8 V. For data before increasing the organic load to 31.8 g / l / day, the standard deviation is the error bar. It showed in. □ is a plot of average values of three experimental results under the condition of −0.6 V (one experimental result in Reference Example A-1 and two experimental results in this Reference Example), and the organic load For data up to 31.8 g / l / day before increasing, the standard deviation is indicated by error bars. Δ is the experimental result under the condition of + 0.0V. The experimental results indicated by ◇ (−0.3V) and ♦ (+ 0.3V) are the results obtained in Reference Example A-1 as they are.

通電無しの条件と−0.6Vの条件については、参考例A−1と同様の傾向が確認された。また、+0.3V及び−0.6Vの条件に加えて、−0.8Vの条件についても、有機物負荷量の増加に伴い、SS除去速度が低下することなく上昇し続けた。特に、−0.6V及び−0.8Vの条件については、有機物負荷量を31.8g/l/日まで増加させても、SS除去速度は低下することなく上昇し続けた。   About the conditions without electricity supply and the conditions of -0.6V, the tendency similar to reference example A-1 was confirmed. Further, in addition to the conditions of +0.3 V and −0.6 V, the condition of −0.8 V also continued to increase without decreasing the SS removal rate as the organic load increased. In particular, under the conditions of −0.6 V and −0.8 V, the SS removal rate continued to increase without decreasing even when the organic load was increased to 31.8 g / l / day.

(4)設定電位と低級脂肪酸濃度の関係
図22に各種設定電位における低級脂肪酸濃度の経時変化を示す。図22において、×は通電無しの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)の平均値をプロットしたものである。○は−0.8Vの条件の3回の実験結果の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。□は−0.6Vの条件の3回の実験結果(参考例A−1における1回の実験結果と本参考例における2回の実験結果)の平均値をプロットしたものであり、有機物負荷量を31.8g/l/日まで増加させる前までのデータについては、標準偏差をエラーバーで示した。△は+0.0Vの条件の実験結果である。◇(−0.3V)、◆(+0.3V)及び▲(+0.6V)で示される実験結果は、参考例A−1で得られた結果をそのまま掲載したものである。
(4) Relationship between set potential and lower fatty acid concentration FIG. 22 shows changes over time in the lower fatty acid concentration at various set potentials. In FIG. 22, x is a plot of average values of three experimental results (one experimental result in Reference Example A-1 and two experimental results in this reference example) under the condition of no energization. ○ is a plot of the average of three experimental results under the condition of -0.8 V. For data before increasing the organic load to 31.8 g / l / day, the standard deviation is the error bar. It showed in. □ is a plot of average values of three experimental results under the condition of −0.6 V (one experimental result in Reference Example A-1 and two experimental results in this Reference Example), and the organic load For data up to 31.8 g / l / day before increasing, the standard deviation is indicated by error bars. Δ is the experimental result under the condition of + 0.0V. The experimental results indicated by ◇ (−0.3V), ♦ (+ 0.3V) and ▲ (+ 0.6V) are the results obtained in Reference Example A-1 as they are.

通電無しの条件と−0.6Vの条件については、参考例A−1と同様の傾向が確認された。また、+0.3V及び−0.6Vの条件に加えて、−0.8Vの条件についても、低級脂肪酸の蓄積が殆ど見られず、特に、−0.6V及び−0.8Vの条件については、有機物負荷量を31.8g/l/日まで増加させても、低級脂肪酸の蓄積は殆ど見られなかった。この結果から、設定電位を+0.3Vと−0.6Vにした場合に加えて、−0.8Vとした場合についても、メタン発酵槽の酸敗を防いで、長期にわたりメタン発酵処理を実施できることが明らかとなった。   About the conditions without electricity supply and the conditions of -0.6V, the tendency similar to reference example A-1 was confirmed. Further, in addition to the conditions of +0.3 V and -0.6 V, the accumulation of lower fatty acids is hardly observed even under the condition of -0.8 V, and particularly with respect to the conditions of -0.6 V and -0.8 V. Even when the organic load was increased to 31.8 g / l / day, accumulation of lower fatty acids was hardly observed. From this result, in addition to the case where the set potential is set to +0.3 V and −0.6 V, also in the case of −0.8 V, it is possible to prevent the methane fermenter from being oxidized and to carry out the methane fermentation treatment over a long period of time. It became clear.

3.まとめ
以上の結果から、作用電極9の電位を、参照電極11である銀・塩化銀電極電位基準で+0.3V、−0.6V、−0.8Vに設定することで、高負荷条件下(有機物負荷量26.9gCOD/l/日)においても、ガス生成速度、COD除去速度、SS除去速度を低下させることなく、また、低級脂肪酸を蓄積させることなく、メタン発酵処理の一連の微生物反応プロセスを進行させることが可能であることが明らかとなった。特に、作用電極9の電位を、参照電極11である銀・塩化銀電極電位基準で−0.6V、−0.8Vに設定することで、さらに高負荷条件下(有機物負荷量31.8gCOD/l/日)においても、ガス生成速度、COD除去速度、SS除去速度を低下させることなく、また、低級脂肪酸を蓄積させることなく、メタン発酵処理の一連の微生物反応プロセスを進行させることが可能であることが明らかとなった。
3. Summary From the above results, by setting the potential of the working electrode 9 to +0.3 V, −0.6 V, and −0.8 V on the basis of the potential of the silver / silver chloride electrode as the reference electrode 11, Even when the organic load is 26.9 g COD / l / day, a series of microbial reaction processes for methane fermentation without reducing the gas production rate, COD removal rate, SS removal rate, and without accumulating lower fatty acids It has become clear that it is possible to proceed. In particular, by setting the potential of the working electrode 9 to −0.6 V and −0.8 V based on the reference potential of the silver / silver chloride electrode as the reference electrode 11, an even higher load condition (organic load 31.8 g COD / 1 / day), it is possible to proceed with a series of microbial reaction processes of methane fermentation without reducing the gas generation rate, COD removal rate, SS removal rate, and without accumulating lower fatty acids. It became clear that there was.

また、設定電位を−0.6Vとした場合と−0.8Vとした場合とでは、ほぼ同様の結果が得られたことから、設定電位を−0.6Vと−0.8Vの間の値に設定した場合にもほぼ同様の結果が得られるものと推定された。このことから、設定電位を+0.3Vまたは−0.6V〜−0.8Vとすることで、高負荷条件下においても、メタン発酵処理の一連の微生物反応プロセスを進行させることが可能であることがわかった。そして、設定電位を−0.6V〜−0.8Vとすることで、SS除去速度の向上効果及び低級脂肪酸の蓄積抑制効果が得られやすくなり、メタン発酵処理の一連の微生物反応プロセスを進行させる上で好適であることがわかった。   In addition, almost the same result was obtained when the set potential was set to -0.6V and -0.8V, and therefore the set potential was a value between -0.6V and -0.8V. It is estimated that almost the same result can be obtained even when set to. From this, by setting the set potential to +0.3 V or −0.6 V to −0.8 V, it is possible to proceed a series of microbial reaction processes of methane fermentation treatment even under high load conditions. I understood. And by making setting potential into -0.6V--0.8V, it becomes easy to acquire the improvement effect of SS removal rate, and the accumulation suppression effect of a lower fatty acid, and a series of microbial reaction processes of a methane fermentation process are advanced. It has been found suitable above.

(参考例B−2)
参考例B−1で新たに加えた条件について、参考例A−2と同様、発酵液各分と担体付着各分とを遺伝子学的解析に供し、微生物の付着状態と微生物群の分布状態について検討した。
(Reference Example B-2)
For the conditions newly added in Reference Example B-1, as in Reference Example A-2, each part of the fermentation broth and each part of the carrier adhering were subjected to genetic analysis, and the adhesion state of microorganisms and the distribution state of microorganism groups investigated.

1.全菌とメタン菌の定量PCR結果
参考例B−1の実験終了後、発酵液の画分と担体付着画分とを取得し、全菌及びメタン菌のコピー数を定量PCRにより測定した。結果を図23〜図26に示す。図23が発酵液画分の全菌のコピー数であり、図24が発酵液画分のメタン菌のコピー数であり、図25が担体付着画分の全菌のコピー数であり、図26が担体付着画分のメタン菌のコピー数である。尚、図23〜図26において、設定電位が−0.3V、+0.3V及び−0.6Vの場合については、基本的には参考例A−2で得られた結果をそのまま掲載したが、一部は再測定した結果を掲載した。
1. Quantitative PCR Results for Whole Bacteria and Methane Bacteria After completion of the experiment of Reference Example B-1, a fraction of the fermentation broth and a carrier-attached fraction were obtained, and the copy numbers of whole bacteria and methane bacteria were measured by quantitative PCR. The results are shown in FIGS. FIG. 23 shows the number of copies of all bacteria in the fermented liquid fraction, FIG. 24 shows the number of copies of methane bacteria in the fermented liquid fraction, FIG. 25 shows the number of copies of all bacteria in the carrier-attached fraction, and FIG. Is the copy number of methane bacteria in the carrier-attached fraction. In FIG. 23 to FIG. 26, for the cases where the set potential is −0.3 V, +0.3 V, and −0.6 V, the results obtained in Reference Example A-2 are basically shown as they are. Some of the results were remeasured.

この結果、担体付着画分については、設定電位が+0.3Vと−0.6Vの場合に加えて、−0.8Vの場合についても、通電無しの場合と比較してコピー数が大幅に増加することが明らかとなった。ところが、発酵液画分については、設定電位が+0.3Vと−0.6Vの場合とは異なり、−0.8Vの場合にはコピー数が減少することが明らかとなった。   As a result, for the carrier-attached fraction, in addition to the case where the set potential is +0.3 V and -0.6 V, the number of copies is greatly increased also in the case of -0.8 V compared to the case where no power is supplied. It became clear to do. However, for the fermented liquor fraction, it was revealed that the copy number decreased when the set potential was -0.8 V, unlike when the set potential was +0.3 V and -0.6 V.

このように、設定電位が−0.8Vの場合には、設定電位が+0.3Vと−0.6Vの場合とは異なり、発酵液画分についてはコピー数が減少する傾向が見られた。それにも関わらず、参考例B−1では、設定電位が+0.3Vと−0.6Vの場合のみならず、−0.8Vの場合にも、高負荷条件においてメタン発酵処理能の維持ないしは向上効果が確認された。このことから、高負荷条件におけるメタン発酵処理能の維持ないしは向上効果には、担体付着画分が大きく寄与していることが明らかとなった。即ち、担体付着画分のコピー数の増加によって、高負荷条件におけるメタン発酵処理能の維持ないしは向上効果が確実に得られることが明らかとなった。   Thus, when the set potential was −0.8 V, unlike the cases where the set potential was +0.3 V and −0.6 V, there was a tendency for the number of copies to decrease for the fermentation broth fraction. Nevertheless, in Reference Example B-1, not only when the set potential is +0.3 V and −0.6 V, but also when the potential is −0.8 V, the maintenance or improvement of the methane fermentation treatment performance under high load conditions. The effect was confirmed. From this, it became clear that the carrier-adhered fraction contributes greatly to the effect of maintaining or improving the methane fermentation treatment performance under high load conditions. That is, it has been clarified that the effect of maintaining or improving the methane fermentation treatment performance under high load conditions can be surely obtained by increasing the copy number of the carrier-attached fraction.

以上の結果から、設定電位を+0.3Vまたは−0.6Vとした場合に加えて、−0.8Vとした場合にも、担体付着画分を増加できることが明らかとなった。また、設定電位を−0.6Vとした場合よりも−0.8Vとした場合の方が担体付着画分が増加したことから、設定電圧を−0.6Vを含んで−0.6Vよりもマイナス側に大きくすれば、担体付着画分の増加効果が得られるものと考えられた。特に、設定電位を−0.6Vとした場合よりも−0.8Vとした場合の方がメタン菌の担体付着画分が大幅に増加していることに鑑みれば、設定電圧を−0.6Vを含んで−0.6Vよりもマイナス側に大きくすれば、担体付着画分の増加効果が得られ、高負荷条件におけるメタン発酵処理能の維持ないしは向上効果が得られるものと考えられた。ここで、模擬有機性廃棄物のボルタンメトリー測定を行った結果を図27に示す。図27に示されるように、設定電位を−1.0Vよりもマイナス側に大きくすると、水分解が起こることが確認された。つまり、設定電位を−1.0Vよりもマイナス側に大きくすると、作用電極からガスが発生し易くなって、目的外の反応が起こる虞があることがわかった。但し、−1.2V程度であれば、水の電気分解はそれほど激しくは起こらないので、−1.2V程度としても、本発明を実施可能であるが、設定電位は−0.6V〜−1.0Vとするのが好適であり、−0.6V〜−0.8Vとするのがより好適であり、−0.8Vとするのがさらに好適であることがわかった。ここで、設定電位を−0.6Vよりもマイナス側に大きな電位に制御すると、作用電極9上で還元反応が生じることから、設定電位は、作用電極9にて還元反応が生じ得る電位とすることが好適であり、尚かつ水の電気分解が激しく起こることのない電位が好適であることがわかった。   From the above results, it has been clarified that the carrier adhesion fraction can be increased when the set potential is −0.8 V in addition to the set potential of +0.3 V or −0.6 V. Further, since the carrier adhering fraction increased when the set potential was set to -0.8 V than when set to -0.6 V, the set voltage including -0.6 V and -0.6 V was exceeded. It was considered that the effect of increasing the fraction adhered to the carrier could be obtained by increasing the value to the minus side. In particular, when the set potential is set to -0.8V, the set voltage is set to -0.6V in view of the fact that the carrier adhering fraction of methane bacteria is greatly increased when set at -0.8V. It was considered that the effect of increasing the fraction adhering to the carrier was obtained and the effect of maintaining or improving the methane fermentation treatment performance under high load conditions was obtained. Here, the result of the voltammetric measurement of the simulated organic waste is shown in FIG. As shown in FIG. 27, it was confirmed that water splitting occurred when the set potential was increased to a minus side from −1.0V. That is, it was found that when the set potential is increased to the minus side from −1.0 V, gas is likely to be generated from the working electrode, and there is a possibility that an unintended reaction may occur. However, since the electrolysis of water does not occur so vigorously at about −1.2V, the present invention can be implemented even at about −1.2V, but the set potential is −0.6V to −1. It was found that the voltage was preferably 0.0 V, more preferably −0.6 V to −0.8 V, and even more preferably −0.8 V. Here, when the set potential is controlled to a potential larger than −0.6 V to the minus side, a reduction reaction occurs on the working electrode 9, so the set potential is set to a potential at which a reduction reaction can occur at the working electrode 9. It has been found that a potential that does not cause vigorous electrolysis of water is suitable.

2.T−RFLPによる細菌群集構造の比較
末端断片長多型解析(T−RFLP)により、全菌のうち、古細菌を除く細菌の群集構造を比較した。結果を図28に示す。図28に示される結果から、設定電位が+0.3Vと−0.6Vの場合に加えて、−0.8Vの場合においても、262bpに該当する微生物、即ち、サーモトガ(Thermotogae)門に属する微生物の占める割合が大きくなり、特に炭素板においてその傾向が顕著であることが明らかとなった。
2. Comparison of bacterial community structure by T-RFLP By end fragment length polymorphism analysis (T-RFLP), the bacterial community structure of all bacteria except archaea was compared. The results are shown in FIG. From the results shown in FIG. 28, in addition to the case where the set potential is +0.3 V and −0.6 V, the microorganism corresponding to 262 bp, that is, the microorganism belonging to the Thermotogae gate, even in the case of −0.8 V It became clear that the ratio which becomes large, and the tendency was remarkable especially in a carbon plate.

また、図28に示される結果から、設定電位が+0.3Vと−0.6Vの場合に加えて、−0.8Vの場合においても、210bpに該当する微生物が検出されなくなった。   Further, from the result shown in FIG. 28, in addition to the case where the set potential is + 0.3V and −0.6V, the microorganism corresponding to 210 bp is not detected even in the case of −0.8V.

以上の結果から、設定電位を+0.3Vまたは−0.6Vとした場合に加えて、設定電位を−0.8Vとした場合にも古細菌を除く細菌の群集構造を制御できることが明らかとなった。   From the above results, it becomes clear that the bacterial community structure excluding archaea can be controlled when the set potential is set to -0.8 V in addition to the set potential set to +0.3 V or -0.6 V. It was.

また、設定電位を−0.6Vとした場合と−0.8Vとした場合とでは、古細菌を除く細菌の群集構造が類似していたことから、設定電位を−0.6Vと−0.8Vの間の値とした場合にもほぼ同様の結果が得られることが考えられた。したがって、設定電位を+0.3Vまたは−0.6V〜−0.8Vとすることで、古細菌を除く細菌の群集構造を制御できることがわかった。   In addition, when the set potential was -0.6 V and -0.8 V, the bacterial community structure except archaea was similar, so the set potential was -0.6 V and -0. It was considered that almost the same result was obtained when the value was between 8V. Therefore, it was found that the bacterial community structure excluding archaea can be controlled by setting the set potential to +0.3 V or −0.6 V to −0.8 V.

そして、さらに解析を進めた結果、設定電位が−0.6Vと−0.8Vの場合に炭素板に付着していた95bp微生物が蛋白質分解能を有すると考えられるBacteroidetes門の細菌に近縁性を示し、150bpの細菌は生ごみの蛋白質や繊維分を特異的に分解していると考えられているFirmicutes門の細菌に近縁性を示すことが確認された。このことから、設定電位を−0.6V〜−0.8Vとすることで、有機性廃棄物のメタン発酵処理に有効な微生物群を担体に付着させる効果があることも明らかとなった。 The result of further analysis, closely related properties to bacteria Bacteroidetes Gate microorganisms 95bp adhering to the carbon plate is considered to have a protein resolution when setting potential of -0.6V and -0.8V The 150 bp bacterium was confirmed to be closely related to the bacteria of the Firmicutes phylum, which is thought to specifically decompose the protein and fiber components of garbage. From this, it was also clarified that setting the set potential to −0.6 V to −0.8 V has an effect of attaching a microorganism group effective for methane fermentation treatment of organic waste to the carrier.

3.T−RFLPによる古細菌群集構造の比較
末端断片長多型解析(T−RFLP)により、全菌のうち、細菌を除く古細菌の群集構造を比較した。尚、古細菌にはメタン生成菌が含まれている。結果を図29に示す。設定電位を−0.8Vとした場合には、設定電位を−0.6Vとした場合と同様に、炭素板において186bpに該当する酢酸資化性メタン生成菌(Methanosarcina thermophila)の占有割合が増加することが明らかとなった。
3. Comparison of archaeal community structure by T-RFLP Comparison of archaea community structure excluding bacteria among all bacteria by end fragment length polymorphism analysis (T-RFLP). The archaebacteria contain methanogens. The results are shown in FIG. When the set potential is set to -0.8 V, the occupation ratio of Methanosarcina thermophila corresponding to 186 bp on the carbon plate increases as in the case where the set potential is set to -0.6 V. It became clear to do.

また、設定電位を−0.6Vとした場合と−0.8Vとした場合の双方で、炭素板において186bpに該当する酢酸資化性メタン生成菌(Methanosarcina thermophila)の占有割合が増加することが明らかとなったことから、設定電位を−0.6Vと−0.8Vの間の値とした場合にもほぼ同様の結果が得られることが考えられた。したがって、設定電位を−0.6V〜−0.8Vとすることで、炭素板上における酢酸資化性メタン生成菌(Methanosarcina thermophila)の占有割合を増加できることがわかった。   In addition, in both the case where the set potential is set to -0.6 V and -0.8 V, the occupation ratio of the methanosarcina thermophila corresponding to 186 bp on the carbon plate may increase. Since it became clear, it was considered that almost the same result could be obtained even when the set potential was set to a value between -0.6V and -0.8V. Therefore, it was found that the occupation ratio of the acetic acid-assimilating methanogen (Methanosarcina thermophila) on the carbon plate can be increased by setting the set potential to −0.6 V to −0.8 V.

以上、T−RFLPによる古細菌群集構造の比較結果から、設定電位を+0.3Vまたは−0.6V〜−0.8Vとすることで、古細菌群集構造を制御することができることが明らかとなった。そして、設定電位を+0.3Vとすることで、炭素板上における水素資化性メタン生成菌の占有割合を増加することができ、設定電位を−0.6V〜−0.8Vとすることで、酢酸資化性メタン生成菌の占有割合を増加することができることが明らかとなった。   As mentioned above, it becomes clear from the comparison result of the archaea community structure by T-RFLP that the archaea community structure can be controlled by setting the set potential to +0.3 V or −0.6 V to −0.8 V. It was. And, by setting the set potential to + 0.3V, the occupation ratio of hydrogen-utilizing methanogens on the carbon plate can be increased, and by setting the set potential to -0.6V to -0.8V. It was revealed that the occupation ratio of acetic acid-utilizing methanogens can be increased.

(実施例1)
作用電極9の炭素板の片面に炭素繊維不織布(炭素繊維不織布(タイプ:ピッチ、空隙率:約98%、径:30.0mm、高さ:70.0mm、厚さ:2.4mm)を接着剤(バスコーク:セメダイン社製)で貼り付けて、上記参考例と同様の実験を行った。但し、酸化還元物質であるAQDSはメタン発酵液4には添加しなかった。したがって、メタン発酵液4の溶液電位の制御性は上記参考例よりも劣るものとなっている。また、基質の組成は、ドッグフード(日本ペットフード製)を100g/L、稲藁0.8g/L、KH2PO4 1.135 g/l, K2HPO4 1.740 g/l, NiCl2・6H2O 0.403 mg/l, CoCl2・6H2O 0.484 mg/lとした。
Example 1
Adhere carbon fiber nonwoven fabric (carbon fiber nonwoven fabric (type: pitch, porosity: about 98%, diameter: 30.0 mm, height: 70.0 mm, thickness: 2.4 mm) to one side of the carbon plate of the working electrode 9. The same experiment as in the above Reference Example was performed, except that AQDS as a redox substance was not added to the methane fermentation broth 4. Therefore, the methane fermentation broth 4 The controllability of the solution potential is inferior to that of the above reference example, and the composition of the substrate is 100 g / L for dog food (manufactured by Nippon Pet Food), 0.8 g / L for rice straw, KH 2 PO 4 1.135 g / l, K 2 HPO 4 1.740 g / l, NiCl 2 .6H 2 O 0.403 mg / l, CoCl 2 .6H 2 O 0.484 mg / l.

運転条件(温度、pH、運転方式)は参考例と同様とした。有機物負荷量と水理学的滞留時間は図36に示す通りとした。   The operating conditions (temperature, pH, operating method) were the same as in the reference example. The organic load and the hydraulic residence time were as shown in FIG.

設定電位は−0.8V、−1.0Vとした。また、比較のために電位制御を行わない場合(コントロール)についても実験を行った。   The set potential was set to -0.8V and -1.0V. For comparison, an experiment was also conducted for the case where no potential control was performed (control).

ガス生成速度の経時変化を図37に示す。コントロールについては、有機物負荷量を27.8gCODcr/L/日とすると、ガス生成速度が低下し始めたのに対し、−0.8Vではこの有機物負荷量においてもガス生成速度が低下することなく、メタン発酵が進行していることが確認された。また、−1.0Vとした場合には、有機物負荷量を32.7gCODcr/L/日としても、高いガス生成速度が得られることが確認された。   FIG. 37 shows changes with time in the gas generation rate. As for the control, when the organic load was 27.8 g CODcr / L / day, the gas generation rate started to decrease, whereas at -0.8 V, the gas generation rate did not decrease even at this organic load. It was confirmed that methane fermentation was in progress. Moreover, when it was set to -1.0V, it was confirmed that a high gas production | generation rate is obtained even if an organic substance load is 32.7gCODcr / L / day.

次に、メタンガス含有率を図38に示す。コントロールについては、有機物負荷量を27.8gCODcr/L/日とすると、メタンガス含有率が大幅に低下した。これに対し、−0.8Vと−1.0Vではこの有機物負荷量においてもメタンガス含有率が低下することなく、−1.0Vについては、有機物負荷量を32.7gCODcr/L/日としてもメタン含有率の低下が見られなかった。   Next, the methane gas content is shown in FIG. As for the control, when the organic load was 27.8 g CODcr / L / day, the methane gas content was greatly reduced. On the other hand, at -0.8V and -1.0V, the methane gas content does not decrease even at this organic load, and at -1.0V, the organic load is 32.7 g CODcr / L / day. No decrease in content was observed.

次に、VFA(低級脂肪酸)濃度の経時変化を図39に示す。コントロールについては、有機物負荷量を27.8gCODcr/L/日とすると、VFA濃度の大幅な増加が見られた。これに対し、−0.8Vと−1.0Vではこの有機物負荷量においてもVFA濃度の大幅な増加は見られず、−1.0Vについては、有機物負荷量を32.7gCODcr/L/日としてもVFA濃度を低濃度に維持できていることが確認された。   Next, FIG. 39 shows changes with time in the VFA (lower fatty acid) concentration. For the control, when the organic load was 27.8 g CODcr / L / day, a significant increase in VFA concentration was observed. On the other hand, at −0.8 V and −1.0 V, no significant increase in VFA concentration was observed even with this organic loading, and for −1.0 V, the organic loading was 32.7 g CODcr / L / day. It was also confirmed that the VFA concentration could be maintained at a low concentration.

次に、COD除去率を図40に示す。コントロールについては、−0.8Vと−1.0Vの場合と比較してCOD除去率が小さい上に、有機物負荷量を27.8gCODcr/L/日とすると、COD除去率が大きく低下する傾向が見られた。これに対し、−0.8Vと−1.0Vではこの有機物負荷量においてもCOD除去率の低下は見られず、−1.0Vについては、有機物負荷量を32.7gCODcr/L/日としてもCOD除去率の低下が見られなかった。   Next, FIG. 40 shows the COD removal rate. Regarding the control, the COD removal rate is small compared to the cases of −0.8 V and −1.0 V, and when the organic load is 27.8 g CODcr / L / day, the COD removal rate tends to be greatly reduced. It was seen. On the other hand, at -0.8 V and -1.0 V, no decrease in COD removal rate was observed even at this organic load, and for -1.0 V, the organic load was 32.7 g CODcr / L / day. No reduction in COD removal rate was observed.

次に、SS除去率を図41に示す。コントロールについては、−0.8Vと−1.0Vの場合と比較してSS除去率が小さい上に、有機物負荷量を27.8gCODcr/L/日とすると、SS除去率が低下する傾向が見られた。これに対し、−0.8Vと−1.0Vではこの有機物負荷量においても40%以上のSS除去率が維持できており、−1.0Vについては、有機物負荷量を32.7gCODcr/L/日としても40%以上のSS除去率が維持できていた。   Next, the SS removal rate is shown in FIG. Regarding the control, the SS removal rate is small compared to the cases of −0.8 V and −1.0 V, and when the organic load is 27.8 g CODcr / L / day, the SS removal rate tends to decrease. It was. On the other hand, at -0.8 V and -1.0 V, the SS removal rate of 40% or more can be maintained even at this organic load, and for -1.0 V, the organic load is 32.7 g CODcr / L / Even on a day, an SS removal rate of 40% or more was maintained.

以上、電極表面に微生物を担持し得る疎水性の担体を備えることで、酸化還元物質をメタン発酵液に添加することなく、27.8gCODcr/L/日という高い有機物負荷量、さらには32.7gCODcr/L/日という極めて高い有機物負荷量においても、メタン発酵処理を安定して行うことが可能であることが明らかとなった。つまり、本発明のメタン発酵処理の構成をとることで、高負荷条件下においても、効率よく連続してメタン発酵処理を実施できることが確認できた。また、本実施例では、酸化還元物質が添加されていないことによって、溶液電位の制御性が低いものとなっていたにも関わらず、上記参考例と同等ないしはそれ以上の有機物負荷量においてもメタン発酵処理を安定して行うことができた。このことから、酸化還元物質を添加することなく、効率よく連続してメタン発酵処理を実施できることも明らかとなった。さらには、稲藁のような分解されにくいリグノセルロース系バイオマスを含む有機性基質を効率よく分解処理できることも明らかとなった。   As described above, by providing a hydrophobic carrier capable of supporting microorganisms on the electrode surface, an organic load amount as high as 27.8 g CODcr / L / day, and further 32.7 g CODcr without adding a redox substance to the methane fermentation solution. It was revealed that the methane fermentation treatment can be stably performed even at an extremely high organic load of / L / day. That is, it has been confirmed that the methane fermentation treatment can be carried out efficiently and continuously even under high load conditions by adopting the configuration of the methane fermentation treatment of the present invention. In addition, in this example, although no redox substance was added, the controllability of the solution potential was low, but even at an organic load amount equal to or higher than that in the above reference example, The fermentation process could be performed stably. From this, it became clear that the methane fermentation treatment can be carried out efficiently and continuously without adding a redox substance. Furthermore, it became clear that an organic substrate containing lignocellulosic biomass that is difficult to be decomposed, such as rice straw, can be efficiently decomposed.

(実施例2)
実施例1における、有機物負荷量27.8gCODcr/L/日(54日目)における発酵液画分及び担体付着画分と、有機物負荷量32.7gCODcr/L/日(62日目)における発酵液画分及び担体付着画分(炭素繊維不織布付着画分)とを、参考例A−1の2の(2)と同様の方法で生物学的分析に供し、発酵液及び担体における微生物の存在状況と、微生物群の分布状態について検討した。
(Example 2)
In Example 1, the fermented liquid fraction and the carrier-adhered fraction at an organic substance load of 27.8 g CODcr / L / day (day 54), and the fermented liquid at an organic substance load of 32.7 g CODcr / L / day (day 62) The fraction and carrier-attached fraction (carbon fiber nonwoven fabric-attached fraction) are subjected to biological analysis in the same manner as in Reference Example A-1 (2), and the presence of microorganisms in the fermentation broth and carrier And the distribution state of the microorganism group was examined.

1.全菌とメタン菌の定量PCR結果
全菌とメタン菌の定量PCR結果を図42〜図45に示す。図42が有機物負荷量27.8gCODcr/L/日における発酵液画分の全菌のコピー数であり、図43が有機物負荷量27.8gCODcr/L/日における担体付着画分の全菌のコピー数であり、図44が有機物負荷量32.7gCODcr/L/日における発酵液画分のメタン菌のコピー数であり、図45が有機物負荷量32.7gCODcr/L/日における担体付着画分のメタン菌のコピー数である。また、全菌とメタン菌の定量PCR結果について纏めた表を表1に示す。
1. Quantitative PCR results of whole bacteria and methane bacteria Quantitative PCR results of whole bacteria and methane bacteria are shown in FIGS. FIG. 42 shows the number of copies of the whole bacteria in the fermented liquid fraction at the organic matter loading of 27.8 g CODcr / L / day, and FIG. 43 shows the copy of the whole bacteria in the carrier-adhered fraction at the organic loading of 27.8 g CODcr / L / day. 44 shows the number of copies of methane bacteria in the fermented liquid fraction at an organic matter loading of 32.7 gCODcr / L / day, and FIG. 45 shows the carrier-attached fraction at an organic matter loading of 32.7 gCODcr / L / day. This is the copy number of methane bacteria. Table 1 summarizes the quantitative PCR results for all bacteria and methane bacteria.

図43及び図45に示されるように、担体付着画分については、全菌及びメタン菌ともに、通電の有無によるコピー数の差はあまり見られなかった。この理由は、担体である炭素繊維不織布はもともと微生物保持効果が高く、電位制御による付着菌数の差異が出にくいことによるものと考えられた。   As shown in FIG. 43 and FIG. 45, regarding the carrier-attached fraction, there was not much difference in the copy number depending on the presence or absence of energization in all the bacteria and methane bacteria. The reason for this was thought to be that the carbon fiber nonwoven fabric as the carrier had a high microorganism-retaining effect and it was difficult to produce a difference in the number of attached bacteria by controlling the potential.

また、図42に示されるように、発酵液画分の全菌のコピー数については、有機物負荷量27.8gCODcr/L/日の場合、通電有り(−0.8V、−1.0V)では、通電無しと比較してコピー数が若干低下する傾向が見られた。有機物負荷量32.7gCODcr/L/日の場合、通電有り(−0.8V、−1.0V)では、通電無しと比較してコピー数が同等かあるいは若干増加する程度であった。   Further, as shown in FIG. 42, regarding the number of copies of all the bacteria in the fermented liquid fraction, when the organic matter load is 27.8 g CODcr / L / day, with energization (−0.8 V, −1.0 V) There was a tendency for the copy number to be slightly lower than when no current was applied. In the case of an organic substance loading of 32.7 g CODcr / L / day, the number of copies was the same or slightly increased in the presence of energization (−0.8 V, −1.0 V) compared to the absence of energization.

また、図44に示されるように、発酵液画分のメタン菌のコピー数については、有機物負荷量27.8gCODcr/L/日の場合、通電有り(−0.8V、−1.0V)では、通電無しと比較してコピー数が増加する傾向が見られた。一方、有機物負荷量32.7gCODcr/L/日の場合、−0.8Vでは通電無しと比較してコピー数が若干増加する傾向が見られたが、−1.0Vでは通電無しと比較してコピー数が若干低下する傾向が見られた。   In addition, as shown in FIG. 44, regarding the copy number of methane bacteria in the fermented liquor fraction, when the organic matter load is 27.8 g CODcr / L / day, with energization (−0.8V, −1.0V) There was a tendency for the number of copies to increase as compared to the case without electricity. On the other hand, when organic load was 32.7 g CODcr / L / day, the copy number tended to increase slightly at -0.8 V compared with no power supply, but at -1.0 V compared with no power supply. There was a tendency for the copy number to decrease slightly.

ここで、発酵液画分について、全菌のコピー数に占めるメタン菌のコピー数の割合を比較すると、有機物負荷量27.8gCODcr/L/日の場合には、−0.8Vで約15.7%、−1.0Vで約21.3%となり、通電無しのとき(約8.2%)と比較して、増加する傾向が見られた。一方で、有機物負荷量32.7gCODcr/L/日の場合には、−0.8Vで約10.1%、−1.0Vで約6.3%となり、通電無しのとき(約8.2%)と比較して、殆ど変わらない傾向が見られた。   Here, when the ratio of the copy number of methane bacteria to the total bacterial copy number is compared with respect to the fermented liquid fraction, in the case of an organic matter load of 27.8 g CODcr / L / day, it is about 15. It was about 21.3% at 7% and -1.0V, and a tendency to increase was observed as compared to the case without energization (about 8.2%). On the other hand, in the case of an organic substance load of 32.7 g CODcr / L / day, it is about 10.1% at -0.8V and about 6.3% at -1.0V, and when no power is supplied (about 8.2 %), There was almost no change.

2.T−RFLPによる古細菌群集構造の比較
末端断片多型解析(T−RFLP)により、全菌のうち、細菌を除く古細菌の群集構造を比較した。結果を図46に示す。
2. Comparison of archaeal community structure by T-RFLP The endocrine polymorphism analysis (T-RFLP) was used to compare the archaeal community structure excluding bacteria. The results are shown in FIG.

解析の結果、参考例A−2の3、参考例B−2の3と同様、メタン生成菌に該当する84bp、92bp、186bp、779bpの4つの末端制限断片(T−RFs)が検出され、発酵液画分及び担体付着画分の古細菌の菌叢は、全てメタン生成菌であることが明らかとなった。因みに、84bpは水素資化性メタン生成菌であるMethanoculleus sp.に該当し、92bpは水素資化性メタン生成菌であるMethanothermobacter sp.に該当し、186bpは酢酸資化性メタン生成菌であるMethanosarcina sp.に該当し、779bpは水素資化性メタン生成菌であるMethanobacterium sp.に該当する。   As a result of analysis, as in Reference Example A-2-3 and Reference Example B-2-3, four end restriction fragments (T-RFs) of 84 bp, 92 bp, 186 bp, and 779 bp corresponding to methanogens were detected. It was revealed that the archaeal flora of the fermented liquid fraction and the carrier-adhered fraction are all methanogens. Incidentally, 84 bp corresponds to Methanoculleus sp. Which is a hydrogen-utilizing methanogen, 92 bp corresponds to Methanothermobacter sp. Which is a hydrogen-utilizing methanogen, and 186 bp is Methanosarcina which is an acetic acid-assimilating methanogen. corresponds to sp., and 779 bp corresponds to Methanobacterium sp., which is a hydrogen-utilizing methanogen.

3.まとめ
定量PCR及び末端断片多型解析の結果から、作用電極の表面に備えられた炭素繊維にメタン生成菌群が付着していることが確認された。このことから、炭素繊維に付着したメタン生成菌群に電子が供給されて活性化されたことによって、実施例1において通電(−0.8V、−1.0V)した場合にメタン発酵処理能が大きく向上したと考えられる。より詳細には、作用電極の表面に備えられた炭素繊維周辺の電位が設定電位と極めて近い電位に制御されることによって、炭素繊維に付着したメタン生成菌群に電子が供給され易くなり、メタン生成菌群の活性化が促され易くなったと考えられる。
3. Summary From the results of quantitative PCR and terminal fragment polymorphism analysis, it was confirmed that methanogenic bacteria were attached to the carbon fibers provided on the surface of the working electrode. From this, by supplying electrons to the methanogenic bacteria group attached to the carbon fibers and activating them, the methane fermentation treatment ability was improved when energized (-0.8 V, -1.0 V) in Example 1. It is thought that it improved greatly. More specifically, by controlling the potential around the carbon fiber provided on the surface of the working electrode to a potential very close to the set potential, electrons can be easily supplied to the methane-producing bacteria group attached to the carbon fiber. It is thought that activation of the producing bacteria group was facilitated.

また、実施例1では、有機物負荷量27.8gCODcr/L/日として通電(−0.8V、−1.0V)した場合に優れたメタン発酵処理能が確認された。この結果と定量PCRにおいて得られた結果について考察すると、発酵液画分における全菌中に占めるメタン菌の割合の増加が、メタン発酵処理能の向上に寄与している可能性が示唆された。そして、発酵液画分における全菌中に占めるメタン菌の割合の増加の要因の一つとして、担体において活性化されたメタン菌が発酵液に供給されたことが考えられる。   Moreover, in Example 1, the outstanding methane fermentation processing capacity was confirmed when it supplied with electricity (-0.8V, -1.0V) as organic substance load amount 27.8gCODcr / L / day. Considering this result and the results obtained in quantitative PCR, it was suggested that an increase in the proportion of methane bacteria in the total bacteria in the fermented liquid fraction may contribute to the improvement of the methane fermentation processability. And as one of the causes of the increase of the ratio of the methane bacterium which occupies in all the bacteria in a fermentation liquid fraction, it is possible that the methane bacterium activated in the support | carrier was supplied to the fermentation liquid.

尚、電極表面に微生物を担持し得る疎水性の担体を備えた場合においても、上記参考例において優れた効果が得られた電位によって、同様の効果が得られるものと推察される。つまり、設定電位を作用電極にて還元反応が生じ得る電位で尚且つ水の電気分解が激しく生じることのない電位または銀・塩化銀電極電位基準で+0.3Vとしても、担体にメタン菌を付着させて、酸化還元物質を用いることなくメタン発酵処理を効率よく進行させ得るものと考えられる。   Even when a hydrophobic carrier capable of supporting microorganisms is provided on the electrode surface, it is presumed that the same effect can be obtained by the potential at which an excellent effect is obtained in the above-mentioned reference example. In other words, even if the set potential is a potential at which the reduction reaction can occur at the working electrode and the electrolysis of water does not occur violently, or +0.3 V based on the silver / silver chloride electrode potential reference, methane bacteria are attached to the carrier. Thus, it is considered that the methane fermentation treatment can proceed efficiently without using a redox substance.

Claims (11)

電極表面の少なくとも一部に疎水性の担体を備えた担体保持電極と有機性基質及びメタン発酵に関与する微生物群を含み且つ前記有機性基質をメタン発酵処理するメタン発酵液とを接触させ、前記担体保持電極の電位を前記担体保持電極から電子が供給される電位または銀・塩化銀電極電位基準で+0.3Vに制御しながらメタン発酵処理を行うことを特徴とするメタン発酵方法。 At least a part comprises a sparse microorganisms involved in the carrier holding electrode and the organic substrate and methane fermentation with the aqueous carrier and the organic substrate of the electrode surface contacting the methane fermentation liquid methane fermentation process, the A methane fermentation method, wherein the methane fermentation treatment is performed while controlling the potential of the carrier holding electrode to +0.3 V based on the potential at which electrons are supplied from the carrier holding electrode or the silver / silver chloride electrode potential. 前記担体保持電極を作用電極とし、
前記作用電極と対電極と参照電極とをポテンシオスタットに結線し、
前記メタン発酵液と電解液とをイオン交換膜を介して接触させ、
前記メタン発酵液に前記作用電極と前記参照電極とを接触させ、
前記電解液に前記対電極を接触させ、
前記作用電極の電位を3電極方式で制御する請求項1に記載のメタン発酵方法。
The carrier holding electrode as a working electrode,
Connecting the working electrode, counter electrode and reference electrode to a potentiostat;
Contacting the methane fermentation broth and electrolyte through an ion exchange membrane;
Bringing the working electrode and the reference electrode into contact with the methane fermentation liquor,
Contacting the counter electrode with the electrolyte;
The methane fermentation method according to claim 1, wherein the potential of the working electrode is controlled by a three-electrode system.
前記担体保持電極を作用電極とし、
前記作用電極と対電極と参照電極とをポテンシオスタットに結線し、
前記メタン発酵液と前記対電極とをイオン交換膜を介して接触させ、
前記メタン発酵液に前記作用電極と前記参照電極とを接触させ、
前記作用電極の電位を3電極方式で制御する請求項1に記載のメタン発酵方法。
The carrier holding electrode as a working electrode,
Connecting the working electrode, counter electrode and reference electrode to a potentiostat;
Contacting the methane fermentation broth and the counter electrode through an ion exchange membrane;
Bringing the working electrode and the reference electrode into contact with the methane fermentation liquor,
The methane fermentation method according to claim 1, wherein the potential of the working electrode is controlled by a three-electrode system.
前記担体保持電極の電位を、前記担体保持電極から電子が供給される電位である−0.8V〜−1.0V(銀・塩化銀電極電位基準)に制御する請求項2または3に記載のメタン発酵方法。 The potential of the carrier holding electrode is controlled to -0.8 V to -1.0 V (silver / silver chloride electrode potential reference), which is a potential at which electrons are supplied from the carrier holding electrode. Methane fermentation method. 前記担体が炭素繊維である請求項1〜4のいずれか1つに記載のメタン発酵方法。 The methane fermentation method according to any one of claims 1 to 4, wherein the carrier is carbon fiber. 電極表面の少なくとも一部に疎水性の担体を備えた担体保持電極と有機性基質及びメタン発酵に関与する微生物群を含み且つ前記有機性基質をメタン発酵処理するメタン発酵液とを接触させ、前記担体保持電極の電位を前記担体保持電極から電子が供給される電位または銀・塩化銀電極電位基準で+0.3Vに制御し、前記担体に前記メタン発酵に関与する微生物群を担持させて活性化させることを特徴とする微生物群が担持された担体の作製方法。 At least a part comprises a sparse microorganisms involved in the carrier holding electrode and the organic substrate and methane fermentation with the aqueous carrier and the organic substrate of the electrode surface contacting the methane fermentation liquid methane fermentation process, the the potential of the carrier holding electrode is controlled to the from the carrier holding electrode electrons by the potential or silver-silver electrode potential reference chloride supplied + 0.3V, by supporting the microorganisms involved in the methane fermentation in the carrier activation A method for producing a carrier on which a microorganism group is supported. 電極表面の少なくとも一部に疎水性の担体を備えた担体保持電極とメタン生成菌群及び前記メタン生成菌群の基質となる物質を少なくとも含む培養液とを接触させ、前記担体保持電極の電位を前記担体保持電極から電子が供給される電位に制御し、前記担体に前記メタン生成菌群を担持させて活性化させることを特徴とする微生物群が担持された担体の作製方法。 The substance is at least in part on the sparse carrier holding electrode and the methanogens group and the methanogens group having the aqueous carrier substrate of the electrode surface in contact with at least containing culture medium, the potential of the carrier holding electrode A method for producing a carrier carrying a microorganism group, characterized by controlling the potential to which electrons are supplied from the carrier holding electrode and causing the carrier to carry and activate the methanogenic bacteria group. 前記担体保持電極を作用電極とし、
前記作用電極と対電極と参照電極とをポテンシオスタットに結線し、
前記メタン発酵液または前記培養液と電解液とをイオン交換膜を介して接触させ、
前記メタン発酵液または前記培養液に前記作用電極と前記参照電極とを接触させ、
前記電解液に前記対電極を接触させ、
前記作用電極の電位を3電極方式で制御する請求項6または7に記載の微生物群が担持された担体の作製方法。
The carrier holding electrode as a working electrode,
Connecting the working electrode, counter electrode and reference electrode to a potentiostat;
The methane fermentation solution or the culture solution and the electrolyte solution are contacted via an ion exchange membrane,
Bringing the working electrode and the reference electrode into contact with the methane fermentation broth or the culture broth;
Contacting the counter electrode with the electrolyte;
The method for producing a carrier carrying a microorganism group according to claim 6 or 7, wherein the potential of the working electrode is controlled by a three-electrode system.
前記担体保持電極を作用電極とし、
前記作用電極と対電極と参照電極とをポテンシオスタットに結線し、
前記メタン発酵液または前記培養液と前記対電極とをイオン交換膜を介して接触させ、
前記メタン発酵液または前記培養液に前記作用電極と前記参照電極とを接触させ、
前記作用電極の電位を3電極方式で制御する請求項6または7に記載の微生物群が担持された担体の作製方法。
The carrier holding electrode as a working electrode,
Connecting the working electrode, counter electrode and reference electrode to a potentiostat;
Contacting the methane fermentation broth or the culture with the counter electrode through an ion exchange membrane;
Bringing the working electrode and the reference electrode into contact with the methane fermentation broth or the culture broth;
The method for producing a carrier carrying a microorganism group according to claim 6 or 7, wherein the potential of the working electrode is controlled by a three-electrode system.
前記担体保持電極の電位を、前記担体保持電極から電子が供給される電位である−0.8V〜−1.0V(銀・塩化銀電極電位基準)に制御する請求項8または9に記載の微生物群が担持された担体の作製方法。 The potential of the carrier holding electrode is controlled to -0.8 V to -1.0 V (silver / silver chloride electrode potential reference) which is a potential at which electrons are supplied from the carrier holding electrode. A method for producing a carrier carrying a microorganism group. 前記担体が炭素繊維である請求項6〜10のいずれか1つに記載の微生物群が担持された担体の作製方法。 The method for producing a carrier carrying a microorganism group according to any one of claims 6 to 10, wherein the carrier is carbon fiber.
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