JP2006255571A - Methane fermentation system and methane fermentation process - Google Patents

Methane fermentation system and methane fermentation process Download PDF

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JP2006255571A
JP2006255571A JP2005075729A JP2005075729A JP2006255571A JP 2006255571 A JP2006255571 A JP 2006255571A JP 2005075729 A JP2005075729 A JP 2005075729A JP 2005075729 A JP2005075729 A JP 2005075729A JP 2006255571 A JP2006255571 A JP 2006255571A
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separated
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sludge
methane fermentation
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JP4611777B2 (en
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Haruo Kurisu
治夫 栗栖
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Sumitomo Heavy Industries Ltd
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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
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Abstract

<P>PROBLEM TO BE SOLVED: To efficiently perform methane fermentation and to facilitate sterilization treatment etc., of a separated liquid. <P>SOLUTION: In addition to the conventional system of returning a part of separated sludge mingled with water so as to be mixed with organic waste on one side where the sludge is subjected to solid-liquid separation by a solid-liquid separation means 3, and in addition to the conventional system of returning a part of the separated liquid mingled with a solid so as to be mixed with the organic waste on the other side where the liquid is subjected to the solid-liquid separation, i.e. returning only a part of the separated sludge, the balance of the separated sludge and the separated liquid is discharged outside the system, thereby roughly discharging the undissolved solid, propagated methane bacteria, and introduced water to be the increased weight components within the system, controlling the inside of a methane fermenter 1 to specified conditions of a desired TS concentration and reducing the emission of the separated liquid to the outside of the system. Even more, further a part of the separated liquid is returned so as to be mixed with the sludge from the methane fermenter 1 to increase the TS concentration within the methane fermenter 1 to the desired TS concentration in the methane fermenter 1. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、メタン発酵システム及びメタン発酵方法に関する。   The present invention relates to a methane fermentation system and a methane fermentation method.

従来、有機性廃棄物をメタン発酵槽でメタン発酵し、このメタン発酵槽の汚泥を沈殿槽で固液分離し、固液分離した分離汚泥の一部をメタン発酵槽に返送する一方で、分離汚泥の残り及び固液分離した分離液を系外に排出する装置が知られている(例えば、特許文献1参照)。この装置にあっては、メタン発酵槽でのメタン発酵により、有機性廃棄物中の固形物の大部分はガス化されて放出される一方で、一部は未分解固形物(残渣)としてメタン発酵槽に残り、さらに一部は増殖メタン菌(固形物)としてメタン発酵槽に残る。また、有機性廃棄物中の水分は、メタン発酵槽にそのまま残る。従って、この未分解固形物、増殖メタン菌、導入水分が、系内での増量分となる。
特開2002−301495号公報
Conventionally, organic waste is methane-fermented in a methane fermentation tank, the sludge of this methane fermentation tank is solid-liquid separated in a precipitation tank, and a part of the separated sludge separated into solid and liquid is returned to the methane fermentation tank, while being separated. An apparatus that discharges the remaining sludge and the separated liquid-solid separation liquid outside the system is known (for example, see Patent Document 1). In this apparatus, most of the solids in the organic waste are gasified and released by methane fermentation in the methane fermenter, while some of the solids in the organic waste are methane as undecomposed solids (residues). It remains in the fermenter, and part of it remains in the methane fermenter as proliferating methane bacteria (solid matter). Moreover, the water | moisture content in organic waste remains as it is in a methane fermentation tank. Therefore, this undecomposed solid matter, proliferating methane bacteria, and introduced water become an increase in the system.
JP 2002-301495 A

ここで、上記公報に記載のようにメタン発酵槽からの汚泥を固液分離するものとして沈殿槽や、例えば機械式のものを用いた場合には、分離汚泥に水分が、分離液に固形分が各々混じると共に、供給される汚泥濃度やその他条件により固形物の回収率が異なることになる。従って、分離汚泥の一部をメタン発酵槽に返送し、分離汚泥の残り及び分離液を系外に排出する上記公報の方式では、前述した系内での増量分となる未分解固形物、増殖メタン菌、導入水分を系外に排出しメタン発酵槽内を所望の高いTS濃度の一定条件とすることはほぼ不可能であり、メタン発酵を効率的に行うことが難しい。   Here, as described in the above publication, when a sludge from a methane fermentation tank is used as a solid-liquid separator, for example, when a mechanical one is used, water is contained in the separated sludge, and solid content is contained in the separated liquid. Are mixed, and the solids recovery rate varies depending on the concentration of sludge supplied and other conditions. Therefore, in the method of the above publication in which a part of the separated sludge is returned to the methane fermentation tank and the remainder of the separated sludge and the separated liquid are discharged out of the system, the above-described undecomposed solid matter, which is an increase in the system, and growth It is almost impossible to discharge methane bacteria and introduced water out of the system to make the inside of the methane fermentation tank have a desired high TS concentration and it is difficult to perform methane fermentation efficiently.

また、系外に排出される分離液に対しては、後段で例えば滅菌処理等が施されることになるが、上記従来技術では分離液の排出量が多く、後段での滅菌処理等が容易では無い。   In addition, the separation liquid discharged out of the system is subjected to, for example, sterilization processing in the subsequent stage, but the above-described conventional technique has a large amount of separation liquid discharged, and the sterilization processing in the subsequent stage is easy. Not.

本発明は、このような課題を解決するために成されたものであり、メタン発酵槽内が所望の高いTS濃度の一定条件とされメタン発酵が効率的に行われると共に、分離液の系外への排出量が低減され後段での分離液の例えば滅菌処理等が容易とされるメタン発酵システム及びメタン発酵方法を提供することを目的とする。   The present invention has been made to solve such problems. The inside of the methane fermenter is set to a constant condition of a desired high TS concentration, and methane fermentation is efficiently performed. It is an object of the present invention to provide a methane fermentation system and a methane fermentation method in which the amount of discharge to the waste water is reduced and the separation liquid in the subsequent stage can be easily sterilized, for example.

本発明によるメタン発酵システムは、有機性廃棄物をメタン発酵するメタン発酵槽と、メタン発酵槽からの汚泥を固液分離する固液分離手段と、固液分離手段で固液分離した分離汚泥の一部を、有機性廃棄物に混合するように返送する分離汚泥返送ラインと、固液分離手段で固液分離した分離液の一部を、有機性廃棄物に混合するように返送する第一の分離液返送ラインと、固液分離手段で固液分離した分離液のさらに一部を、メタン発酵槽からの汚泥に混合するように返送する第二の分離液返送ラインと、固液分離手段で固液分離した分離汚泥の残りを系外に排出する分離汚泥排出ラインと、固液分離手段で固液分離した分離液の残りを系外に排出する分離液排出ラインと、を具備したことを特徴としている。   The methane fermentation system according to the present invention includes a methane fermentation tank for methane fermentation of organic waste, a solid-liquid separation means for solid-liquid separation of sludge from the methane fermentation tank, and a separated sludge separated by solid-liquid separation by the solid-liquid separation means. A separation sludge return line that returns a part to be mixed with organic waste, and a part of the separated liquid that has been solid-liquid separated by solid-liquid separation means is returned to be mixed with organic waste. A separate liquid return line, a second separate liquid return line for returning a part of the separated liquid separated by the solid-liquid separation means so as to be mixed with the sludge from the methane fermentation tank, and the solid-liquid separation means A separation sludge discharge line that discharges the remainder of the separated sludge separated into solid and liquid at the outside of the system and a separation liquid discharge line that discharges the remainder of the separated liquid separated by the solid-liquid separation means to the outside of the system. It is characterized by.

また、本発明によるメタン発酵方法は、有機性廃棄物をメタン発酵槽でメタン発酵し、このメタン発酵槽からの汚泥を固液分離手段で固液分離し、固液分離手段で固液分離した分離汚泥の一部及び固液分離手段で固液分離した分離液の一部を、有機性廃棄物に混合するように返送すると共に、固液分離手段で固液分離した分離液のさらに一部を、メタン発酵槽からの汚泥に混合するように返送し、固液分離手段で固液分離した分離汚泥の残り及び固液分離手段で固液分離した分離液の残りを系外に排出することを特徴としている。   In the methane fermentation method according to the present invention, organic waste is methane-fermented in a methane fermentation tank, and sludge from the methane fermentation tank is solid-liquid separated by solid-liquid separation means, and solid-liquid separation is performed by solid-liquid separation means. A part of the separated sludge and a part of the separated liquid separated by the solid-liquid separating means are returned to be mixed with the organic waste, and a part of the separated liquid separated by the solid-liquid separating means is further returned. Is mixed with sludge from the methane fermentation tank and the remainder of the separated sludge separated by solid-liquid separation by the solid-liquid separation means and the remainder of the separated liquid separated by solid-liquid separation by the solid-liquid separation means are discharged out of the system. It is characterized by.

このようなメタン発酵システム及びメタン発酵方法によれば、固液分離した一方側であり水分が混じる分離汚泥のその一部を有機性廃棄物に混合するように返送する従来方式に加えて、固液分離した他方側であり固形物が混じる分離液のその一部を有機性廃棄物に混合するように返送すると共に分離液のさらに一部をメタン発酵槽からの汚泥に混合するように返送し、すなわち固液分離した分離汚泥の一部のみを返送する従来方式に加えて固液分離した分離液の一部も返送し、分離汚泥及び分離液の残りを系外に排出するようにしているため、系内での増量分となる未分解固形物、増殖メタン菌、導入水分を系外に概ね排出することが可能とされメタン発酵槽内を所望のTS濃度の一定条件とすることが可能とされると共に、分離液の系外への排出量を低減することが可能とされる。しかも、このように分離液のさらに一部をメタン発酵槽からの汚泥に混合するように返送しているため、メタン発酵槽内のTS濃度を所望に高めることが可能とされる。   According to such a methane fermentation system and methane fermentation method, in addition to the conventional method of returning a part of the separated sludge mixed with water on one side of the solid-liquid separation to be mixed with the organic waste, Return the part of the separated liquid mixed with solids to the organic waste and return another part of the separated liquid to the sludge from the methane fermentation tank. In other words, in addition to the conventional method of returning only a part of the separated sludge after solid-liquid separation, a part of the separated liquid separated by solid-liquid separation is also returned, and the separated sludge and the remaining liquid are discharged out of the system. Therefore, undegraded solid matter, proliferating methane bacteria, and introduced water that are increased in the system can be discharged out of the system, and the inside of the methane fermenter can be set to a constant condition of the desired TS concentration. And the separation liquid out of the system Is it possible to reduce emissions. Moreover, since a part of the separated liquid is returned to be mixed with the sludge from the methane fermentation tank, the TS concentration in the methane fermentation tank can be increased as desired.

ここで、固液分離した分離汚泥に水分が混じり、固液分離した分離液に固形分が混じる固液分離手段としては、具体的には、機械式又は沈殿式の固液分離手段が挙げられる。   Here, specific examples of the solid-liquid separation means in which water is mixed in the separated sludge after solid-liquid separation and the solid content is mixed in the separated liquid-solid separation liquid include mechanical or precipitation type solid-liquid separation means. .

このように本発明によれば、メタン発酵槽内を所望の高いTS濃度の一定条件とすることが可能とされるため、メタン発酵を効率的に行うことが可能になると共に、分離液の系外への排出量を低減することが可能とされるため、後段での分離液の例えば滅菌処理等を容易とすることが可能となる。   As described above, according to the present invention, the inside of the methane fermentation tank can be set to a constant condition with a desired high TS concentration, so that methane fermentation can be performed efficiently and the system of the separated liquid Since it is possible to reduce the discharge amount to the outside, it is possible to facilitate, for example, sterilization of the separated liquid in the subsequent stage.

以下、本発明によるメタン発酵システム及びメタン発酵方法の好適な実施形態について図面を参照しながら説明する。図1は、本発明の実施形態に係るメタン発酵システムを示す概略構成図であり、例えば廃棄物処理設備等に採用されるものである。   Hereinafter, preferred embodiments of a methane fermentation system and a methane fermentation method according to the present invention will be described with reference to the drawings. FIG. 1 is a schematic configuration diagram showing a methane fermentation system according to an embodiment of the present invention, which is employed in, for example, a waste treatment facility.

図1に示すように、メタン発酵システム100は、メタン発酵槽1、混合槽2、固液分離手段3をこの順に接続して備えると共に、固液分離手段3の分離汚泥排出側とメタン発酵槽1とを接続する分離汚泥返送ラインL1、この分離汚泥返送ラインL1の途中で分岐される分離汚泥排出ラインL4、固液分離手段3の分離液排出側とメタン発酵槽1とを接続する第一の分離液返送ラインL2、固液分離手段3の分離液排出側と混合槽2とを接続する第二の分離液返送ラインL3、これらの分離液返送ラインL2,L3の途中で分岐される分離液排出ラインL5を備え、導入される有機性廃棄物を所定にメタン発酵処理するものである。そして、ここでは、有機性廃棄物として、食品残渣等の含水固形物(家庭ごみ等)が高濃度の有機性廃棄物として導入される。   As shown in FIG. 1, the methane fermentation system 100 includes a methane fermentation tank 1, a mixing tank 2, and a solid-liquid separation unit 3 connected in this order, and a separated sludge discharge side of the solid-liquid separation unit 3 and a methane fermentation tank. 1 connected to the methane fermentation tank 1 and the separated sludge discharge line L4 branched in the middle of the separated sludge return line L1, the separated liquid discharge side of the solid-liquid separation means 3, and the methane fermentation tank 1. The separated liquid return line L2, the second separated liquid return line L3 connecting the separation liquid discharge side of the solid-liquid separation means 3 and the mixing tank 2, and the separation branched in the middle of these separated liquid return lines L2 and L3. A liquid discharge line L5 is provided, and the introduced organic waste is subjected to a predetermined methane fermentation treatment. And here, water-containing solids (such as household waste) such as food residues are introduced as organic waste as high-concentration organic waste.

メタン発酵槽1は、導入される有機性廃棄物、分離汚泥返送ラインL1を介して返送される分離汚泥の一部、及び、第一の分離液返送ラインL2を介して返送される分離液の一部を撹拌機により撹拌しながらメタン発酵し、メタンと二酸化炭素を主成分とするバイオガスを生成するものである。このメタン発酵槽1で生成されたバイオガスは、例えば、ガスエンジンや燃料電池といった発電機やボイラの燃料として用いられる。また、バイオガス中のメタンを、例えば、気体分離膜方式、PSA方式又は加圧水吸収方式等により濃縮することで、自動車燃料等として利用される。   The methane fermentation tank 1 is composed of the organic waste to be introduced, a part of the separated sludge returned via the separated sludge return line L1, and the separated liquid returned via the first separated liquid return line L2. A portion of the mixture is stirred with a stirrer and methane-fermented to produce biogas mainly composed of methane and carbon dioxide. The biogas produced in the methane fermentation tank 1 is used as a fuel for generators and boilers such as gas engines and fuel cells, for example. Further, methane in biogas is used as an automobile fuel or the like by concentrating it by, for example, a gas separation membrane method, a PSA method, or a pressurized water absorption method.

このメタン発酵槽1に接続される混合槽2は、メタン発酵槽1からの汚泥及び第二の分離液返送ラインL3を介して返送される分離液のさらに一部を、撹拌機の撹拌により混合し、性状を均一化するものである。   The mixing tank 2 connected to the methane fermentation tank 1 mixes the sludge from the methane fermentation tank 1 and a further part of the separated liquid returned via the second separated liquid return line L3 by stirring with a stirrer. And uniform properties.

この混合槽2に接続される固液分離手段3は、混合槽2からの汚泥を固形物と液体とに分離するためのものであり、分離汚泥と分離液とに分離する。この固液分離手段3としては、例えば、スクリュープレス脱水機、遠心脱水機、フィルタープレス脱水機、ベルトプレス脱水機、多重円板脱水機等の機械式の固液分離手段、又は、沈殿式(沈降分離式)の固液分離手段(沈殿槽)が用いられる。   The solid-liquid separation means 3 connected to the mixing tank 2 is for separating the sludge from the mixing tank 2 into a solid and a liquid, and separates it into a separated sludge and a separated liquid. Examples of the solid-liquid separation means 3 include mechanical solid-liquid separation means such as a screw press dehydrator, a centrifugal dehydrator, a filter press dehydrator, a belt press dehydrator, a multi-disc dehydrator, or a precipitation type ( A solid-liquid separation means (precipitation tank) of a sedimentation separation type) is used.

固液分離手段3の分離汚泥排出側とメタン発酵槽1とを接続する分離汚泥返送ラインL1は、固液分離手段3からの分離汚泥の一部をメタン発酵槽1に返送する。一方、固液分離手段3の分離液排出側とメタン発酵槽1とを接続する第一の分離汚泥返送ラインL2は、固液分離手段3からの分離液の一部をメタン発酵槽1に返送する。また、固液分離手段3の分離液排出側と混合槽2とを接続する第二の分離汚泥返送ラインL3は、固液分離手段3からの分離液のさらに一部を混合槽2に返送する。   A separation sludge return line L1 connecting the separated sludge discharge side of the solid-liquid separation means 3 and the methane fermentation tank 1 returns a part of the separated sludge from the solid-liquid separation means 3 to the methane fermentation tank 1. On the other hand, the first separation sludge return line L2 connecting the separation liquid discharge side of the solid-liquid separation means 3 and the methane fermentation tank 1 returns a part of the separation liquid from the solid-liquid separation means 3 to the methane fermentation tank 1. To do. The second separation sludge return line L3 connecting the separation liquid discharge side of the solid-liquid separation means 3 and the mixing tank 2 returns a further part of the separation liquid from the solid-liquid separation means 3 to the mixing tank 2. .

また、分離汚泥返送ラインL1から分岐された分離汚泥排出ラインL4は、分離汚泥の残りを系外に排出し、第一、第二の分離液返送ラインL2,L3から分岐された分離液排出ラインL5は、分離液の残りを系外に排出し河川等に放流すべく後段の滅菌処理に供する。   The separated sludge discharge line L4 branched from the separated sludge return line L1 discharges the remainder of the separated sludge outside the system, and the separated liquid discharge line branched from the first and second separated liquid return lines L2 and L3. L5 is subjected to a subsequent sterilization treatment to discharge the remainder of the separation liquid out of the system and discharge it to a river or the like.

次に、このように構成されたメタン発酵システム100の作用について説明する。導入された有機性廃棄物は、メタン発酵槽1で、固液分離手段3から分離汚泥返送ラインL1を介して返送される分離汚泥の一部及び固液分離手段3から第一の分離液返送ラインL2を介して返送される分離液の一部と混合され、この分離汚泥及び分離液の返送により所望の高いTS濃度とされたメタン発酵槽1においてメタン発酵される。   Next, the effect | action of the methane fermentation system 100 comprised in this way is demonstrated. The introduced organic waste is a part of the separated sludge returned from the solid-liquid separation means 3 via the separated sludge return line L1 and the first separated liquid return from the solid-liquid separation means 3 in the methane fermentation tank 1. It is mixed with a part of the separated liquid returned via the line L2, and is subjected to methane fermentation in the methane fermentation tank 1 having a desired high TS concentration by returning the separated sludge and the separated liquid.

このメタン発酵槽1でのメタン発酵により、有機性廃棄物中の固形物の大部分はガス化されバイオガスとして放出されて所定に利用され、一部は未分解固形物(残渣)としてメタン発酵槽1に残り、さらに一部は増殖メタン菌(固形物)としてメタン発酵槽1に残る。一方、有機性廃棄物中の水分は、メタン発酵槽1にそのまま残る(ごく一部の水分はガス化し、反応によりごく少量の水は発生する)。   By the methane fermentation in the methane fermenter 1, most of the solids in the organic waste are gasified and released as biogas, and are used as they are, and some of them are methane fermentation as undecomposed solids (residues). It remains in the tank 1, and a part further remains in the methane fermenter 1 as proliferating methane bacteria (solid matter). On the other hand, the water in the organic waste remains in the methane fermentation tank 1 (a part of the water is gasified and a very small amount of water is generated by the reaction).

この未分解固形物、増殖メタン菌、導入水分が、メタン発酵槽1での増量分となり、メタン発酵槽1内を所望のTS濃度の一定条件(メタン発酵槽1内の液面の増減が無い、TS濃度が一定)とするには、この増量分を系外に排出する必要があるが、これについては後述する。   This undecomposed solid matter, proliferating methane bacteria, and introduced water become an increased amount in the methane fermentation tank 1, and there is no increase or decrease in the liquid level in the methane fermentation tank 1 within the methane fermentation tank 1 under a certain condition of a desired TS concentration. In order to make the TS concentration constant), this increased amount needs to be discharged out of the system, which will be described later.

メタン発酵槽1の汚泥は、混合槽2で固液分離手段3から第二の分離液返送ラインL3を介して返送される分離液のさらに一部と混合され、この混合槽2の汚泥は、固液分離手段3で分離汚泥と分離液とに固液分離される。   The sludge in the methane fermentation tank 1 is mixed with a part of the separated liquid returned from the solid-liquid separation means 3 through the second separated liquid return line L3 in the mixing tank 2, and the sludge in the mixing tank 2 is Solid-liquid separation is performed by the solid-liquid separation means 3 into separated sludge and separated liquid.

ここで、固液分離手段3としては、前述のように、機械式又は沈殿式が用いられているため、固液分離した分離汚泥には水分が、固液分離した分離液には固形分が各々混じると共に、供給される汚泥濃度やその他条件により固形物の回収率が異なることになる。従って、従来のような分離汚泥の一部をメタン発酵槽に返送し分離汚泥の残り及び分離液の全部を系外に排出する方式では、系内での増量分となる未分解固形物、増殖メタン菌、導入水分を系外に排出しメタン発酵槽内を所望の高いTS濃度の一定条件とすることはほぼ不可能である。   Here, as the solid-liquid separation means 3, as described above, since a mechanical type or a precipitation type is used, moisture is contained in the separated sludge after solid-liquid separation, and solid content is contained in the separated liquid-solid separated liquid. As they are mixed, the solids recovery rate varies depending on the supplied sludge concentration and other conditions. Therefore, in the conventional method in which a part of the separated sludge is returned to the methane fermentation tank and the remainder of the separated sludge and the whole of the separated liquid are discharged out of the system, undecomposed solid matter that increases in the system, growth It is almost impossible to discharge the methane bacteria and the introduced water out of the system to make the inside of the methane fermentation tank have a desired high TS concentration constant condition.

しかしながら、本実施形態においては、固液分離手段3の分離汚泥の一部が分離汚泥返送ラインL1によりメタン発酵槽1に返送されると共に分離液の一部が第一の分離液返送ラインL2によりメタン発酵槽1に返送され、分離液のさらに一部が第二の分離液返送ラインL3により混合槽2に返送され、一方、分離汚泥の残りが分離汚泥排出ラインL4を介して系外に排出されると共に、分離液の残りが分離液排出ラインL5を介して系外に排出される。   However, in this embodiment, a part of the separated sludge of the solid-liquid separation means 3 is returned to the methane fermentation tank 1 by the separated sludge return line L1, and a part of the separated liquid is sent by the first separated liquid return line L2. It is returned to the methane fermentation tank 1, and a part of the separated liquid is returned to the mixing tank 2 through the second separated liquid return line L3, while the remaining separated sludge is discharged out of the system through the separated sludge discharge line L4. At the same time, the remainder of the separation liquid is discharged out of the system through the separation liquid discharge line L5.

このように、本実施形態では、固液分離した一方側であり水分が混じる分離汚泥のその一部を有機性廃棄物に混合するように返送する従来方式に加えて、固液分離した他方側であり固形物が混じる分離液のその一部を有機性廃棄物に混合するように返送すると共に分離液のさらに一部をメタン発酵槽1からの汚泥に混合するように返送し、すなわち固液分離した分離汚泥の一部のみを返送する従来方式に加えて固液分離した分離液の一部も返送し、分離汚泥及び分離液の残りを系外に排出するようにしているため、系内での増量分となる未分解固形物、増殖メタン菌、導入水分を系外に概ね排出することが可能とされメタン発酵槽1内を所望のTS濃度の一定条件とすることが可能とされると共に、分離液の系外への排出量を低減することが可能とされる。しかも、このように分離液のさらに一部をメタン発酵槽1からの汚泥に混合するように返送しているため、メタン発酵槽1内のTS濃度を所望に高めることが可能とされる。これらの結果、メタン発酵を効率的に行うこと、及び、後段での分離液の滅菌処理等を容易とすることが可能とされる。なお、本実施形態にあっては、種汚泥の投入及び加水の必要は無い。   As described above, in this embodiment, in addition to the conventional method in which a part of the separated sludge mixed with water and mixed with the organic waste is returned on one side of the solid-liquid separation, the other side subjected to the solid-liquid separation. And a part of the separated liquid mixed with the solid matter is returned to be mixed with the organic waste, and a part of the separated liquid is returned to be mixed with the sludge from the methane fermentation tank 1, that is, the solid liquid In addition to the conventional method in which only a part of the separated sludge is returned, a part of the separated liquid that has been solid-liquid separated is also returned, and the separated sludge and the remaining liquid are discharged outside the system. The amount of undegraded solids, proliferating methane bacteria, and introduced water that are to be increased in the system can be discharged out of the system, and the inside of the methane fermenter 1 can be set to a constant condition of a desired TS concentration. At the same time, it is possible to reduce the amount of separation liquid discharged outside the system. It is a function. Moreover, since a part of the separated liquid is returned so as to be mixed with the sludge from the methane fermentation tank 1, the TS concentration in the methane fermentation tank 1 can be increased as desired. As a result, it is possible to efficiently perform methane fermentation and facilitate sterilization of the separated liquid in the subsequent stage. In this embodiment, it is not necessary to add seed sludge and add water.

図2は、図1のメタン発酵システム100の物質収支の一例を示す図であり、固液分離手段3の分離汚泥のTS回収率が70%の時のものである。ここでは、食品糟25kg(水分18.75kg、TS(固形物)6.25kg;TS濃度25%)が有機性廃棄物として導入されている。この有機性廃棄物が、TS濃度4%のメタン発酵槽1でメタン発酵され、バイオガス4.4kgが放出される一方で、未分解固形物及び増殖メタン菌1.85kg、水分18.75kgの混合物(TS濃度8.98%)が系内の増加分として残る。   FIG. 2 is a diagram showing an example of the material balance of the methane fermentation system 100 of FIG. 1, and is when the TS recovery rate of the separated sludge of the solid-liquid separation means 3 is 70%. Here, 25 kg of food waste (moisture 18.75 kg, TS (solid matter) 6.25 kg; TS concentration 25%) is introduced as organic waste. This organic waste is methane-fermented in a methane fermenter 1 having a TS concentration of 4%, and 4.4 kg of biogas is released. On the other hand, 1.85 kg of undecomposed solid matter and proliferating methane bacteria and water of 18.75 kg The mixture (TS concentration 8.98%) remains as an increase in the system.

ここで、メタン発酵槽1のTS濃度を4%として系内のバランスを保つには、図2に示すように、分離汚泥の一部1.54kg(水分1.39kg、TS0.15kg)をメタン発酵槽1に返送すると共に、分離液の一部27.86kgをメタン発酵槽1に返送し、分離液のさらに一部164kgを混合槽2に返送すれば良い。これにより、メタン発酵槽1のTS濃度が4%に保たれると共に、分離汚泥の残り12.5kg(水分11.2kg、TS1.25kg)及び分離液の残り7.6kg(水分7.54kg、TS0.02kg)が系外に排出され、系内での増量分となる未分解固形物、増殖メタン菌、導入水分が系外に概ね排出される。   Here, in order to maintain the balance in the system by setting the TS concentration in the methane fermenter 1 to 4%, as shown in FIG. 2, 1.54 kg (moisture 1.39 kg, TS 0.15 kg) of the separated sludge is methane. While returning to the fermenter 1, a part of 27.86 kg of the separated liquid may be returned to the methane fermenter 1, and a further part of 164 kg of the separated liquid may be returned to the mixing tank 2. As a result, the TS concentration in the methane fermentation tank 1 is maintained at 4%, and the remaining 12.5 kg of separated sludge (moisture 11.2 kg, TS 1.25 kg) and the remaining liquid 7.6 kg (moisture 7.54 kg, TS0.02 kg) is discharged out of the system, and undecomposed solid matter, proliferating methane bacteria, and introduced water that are increased in the system are generally discharged out of the system.

以上、本発明をその実施形態に基づき具体的に説明したが、本発明は上記実施形態に限定されるものではない。例えば、上記実施形態においては、分離汚泥の一部を分離汚泥返送ラインL1により、分離液の一部を第一の分離液返送ラインL2によりメタン発酵槽1に返送するようにしているが、有機性廃棄物をメタン発酵槽1に移送するラインに返送しても良く、また、メタン発酵槽1の前段に有機性廃棄物が流入する例えば酸生成槽を設ける場合には当該酸生成槽に返送するようにしても良く、要は、有機性廃棄物に混合するように返送できれば良い。   As mentioned above, although this invention was concretely demonstrated based on the embodiment, this invention is not limited to the said embodiment. For example, in the above embodiment, a part of the separated sludge is returned to the methane fermentation tank 1 by the separated sludge return line L1, and a part of the separated liquid is returned to the methane fermentation tank 1 by the first separated liquid return line L2. The organic waste may be returned to the line for transferring the organic waste to the methane fermentation tank 1, and when an acid generation tank is provided, for example, where the organic waste flows into the preceding stage of the methane fermentation tank 1, it is returned to the acid generation tank In short, it suffices if it can be returned to be mixed with organic waste.

また、上記実施形態においては、分離液のさらに一部を第二の分離液返送ラインL3により混合槽2に返送するようにしているが、メタン発酵槽1の汚泥を混合槽2に移送するラインに返送しても良い。また、混合槽2は無くても良く、この場合には、メタン発酵槽1の汚泥を固液分離手段3に移送するラインに返送すれば良く、要は、メタン発酵槽1からの汚泥に混合するように返送できれば良い。   Moreover, in the said embodiment, although a part of separation liquid is returned to the mixing tank 2 by the 2nd separated liquid return line L3, the line which transfers the sludge of the methane fermentation tank 1 to the mixing tank 2 You may return it to Further, the mixing tank 2 may be omitted, and in this case, the sludge from the methane fermentation tank 1 may be returned to the line for transferring to the solid-liquid separation means 3. I just need to be able to return it.

また、上記実施形態においては、特に好適であるとして、食品残渣等の含水固形物を高濃度の有機性廃棄物として対象としているが、高濃度の液状有機性廃棄物であっても良く、要は、有機性廃棄物全般に対して適用可能である。   Further, in the above-described embodiment, water solids such as food residues are targeted as high-concentration organic wastes as being particularly suitable, but high-concentration liquid organic wastes may be used. Is applicable to all organic waste.

本発明の実施形態に係るメタン発酵システムを示す概略構成図である。It is a schematic structure figure showing a methane fermentation system concerning an embodiment of the present invention. 図1のメタン発酵システムの物質収支の一例を示す図である。It is a figure which shows an example of the material balance of the methane fermentation system of FIG.

符号の説明Explanation of symbols

1…メタン発酵槽、2…混合槽、3…固液分離手段、100…メタン発酵システム、L1…分離汚泥返送ライン、L2…第一の分離液返送ライン、L3…第二の分離液返送ライン、L4…分離汚泥排出ライン、L5…分離液排出ライン。
DESCRIPTION OF SYMBOLS 1 ... Methane fermentation tank, 2 ... Mixing tank, 3 ... Solid-liquid separation means, 100 ... Methane fermentation system, L1 ... Separation sludge return line, L2 ... First separation liquid return line, L3 ... Second separation liquid return line , L4 ... separation sludge discharge line, L5 ... separation liquid discharge line.

Claims (3)

有機性廃棄物をメタン発酵するメタン発酵槽と、
前記メタン発酵槽からの汚泥を固液分離する固液分離手段と、
前記固液分離手段で固液分離した分離汚泥の一部を、前記有機性廃棄物に混合するように返送する分離汚泥返送ラインと、
前記固液分離手段で固液分離した分離液の一部を、前記有機性廃棄物に混合するように返送する第一の分離液返送ラインと、
前記固液分離手段で固液分離した分離液のさらに一部を、前記メタン発酵槽からの汚泥に混合するように返送する第二の分離液返送ラインと、
前記固液分離手段で固液分離した分離汚泥の残りを系外に排出する分離汚泥排出ラインと、
前記固液分離手段で固液分離した分離液の残りを系外に排出する分離液排出ラインと、を具備したメタン発酵システム。
A methane fermentation tank for methane fermentation of organic waste,
Solid-liquid separation means for solid-liquid separation of the sludge from the methane fermentation tank;
A separated sludge return line for returning a part of the separated sludge separated by solid-liquid separation by the solid-liquid separation means to be mixed with the organic waste,
A first separated liquid return line for returning a part of the separated liquid separated by the solid-liquid separation means so as to be mixed with the organic waste;
A second separated liquid return line for returning a further part of the separated liquid separated by the solid-liquid separation means so as to be mixed with the sludge from the methane fermentation tank;
A separation sludge discharge line for discharging the remaining sludge separated by the solid-liquid separation means out of the system;
A methane fermentation system comprising: a separation liquid discharge line for discharging the remainder of the separation liquid solid-liquid separated by the solid-liquid separation means to the outside of the system.
前記固液分離手段は、機械式又は沈殿式であることを特徴とする請求項1記載のメタン発酵システム。   The methane fermentation system according to claim 1, wherein the solid-liquid separation means is a mechanical type or a precipitation type. 有機性廃棄物をメタン発酵槽でメタン発酵し、
このメタン発酵槽からの汚泥を固液分離手段で固液分離し、
前記固液分離手段で固液分離した分離汚泥の一部及び前記固液分離手段で固液分離した分離液の一部を、前記有機性廃棄物に混合するように返送すると共に、前記固液分離手段で固液分離した分離液のさらに一部を、前記メタン発酵槽からの汚泥に混合するように返送し、
前記固液分離手段で固液分離した分離汚泥の残り及び前記固液分離手段で固液分離した分離液の残りを系外に排出することを特徴とするメタン発酵方法。
Organic waste is methane fermented in a methane fermenter,
The sludge from this methane fermentation tank is solid-liquid separated by solid-liquid separation means,
A part of the separated sludge separated by solid-liquid separation by the solid-liquid separation means and a part of the separated liquid separated by solid-liquid separation means are returned so as to be mixed with the organic waste, and the solid-liquid Return a further part of the separated liquid separated by the separation means to be mixed with the sludge from the methane fermentation tank,
A methane fermentation method characterized by discharging the remainder of the separated sludge solid-liquid separated by the solid-liquid separation means and the remainder of the separated liquid solid-liquid separated by the solid-liquid separation means to the outside of the system.
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2011071013A1 (en) * 2009-12-09 2011-06-16 メタウォーター株式会社 Methane fermentation method and methane fermentation device
JP2011143326A (en) * 2010-01-12 2011-07-28 Takuma Co Ltd Dry type methane fermentation residue dehydration system
WO2014093799A1 (en) * 2012-12-14 2014-06-19 Bp Corporation North America Inc. Process for the conversion of cellulosic feedstock materials
KR102023639B1 (en) * 2018-11-30 2019-09-20 주식회사 환경에너지오앤엠 High-rate dry anaerobic digestion apparatus for treatment of high concentration organic wastes

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10330179A (en) * 1997-05-29 1998-12-15 Ebara Corp Method for composting anaerobic digested sludge
JPH1177007A (en) * 1997-09-02 1999-03-23 Ebara Corp Anaerobic digestion of organic waste
JP2003112145A (en) * 2001-10-01 2003-04-15 Kobe Steel Ltd Anaerobic treatment method for organic waste and apparatus therefor
JP2003117594A (en) * 2001-10-12 2003-04-22 Ebara Corp Treating method and treating equipment for organic sewage
JP2003290751A (en) * 2002-04-01 2003-10-14 Sumitomo Heavy Ind Ltd Device and method for methane fermentation treatment
JP2003320394A (en) * 2002-04-30 2003-11-11 Kurita Water Ind Ltd Treatment apparatus and treatment method for organic waste
JP2004160406A (en) * 2002-11-14 2004-06-10 Hokoku Kogyo Co Ltd Ammonia concentration automatic control method in biogas conversion and treatment apparatus for organic waste using the same
JP2004230273A (en) * 2003-01-30 2004-08-19 Mitsubishi Kakoki Kaisha Ltd Method for treating organic waste
JP2004249233A (en) * 2003-02-21 2004-09-09 Mitsubishi Kakoki Kaisha Ltd Method for treating organic waste

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10330179A (en) * 1997-05-29 1998-12-15 Ebara Corp Method for composting anaerobic digested sludge
JPH1177007A (en) * 1997-09-02 1999-03-23 Ebara Corp Anaerobic digestion of organic waste
JP2003112145A (en) * 2001-10-01 2003-04-15 Kobe Steel Ltd Anaerobic treatment method for organic waste and apparatus therefor
JP2003117594A (en) * 2001-10-12 2003-04-22 Ebara Corp Treating method and treating equipment for organic sewage
JP2003290751A (en) * 2002-04-01 2003-10-14 Sumitomo Heavy Ind Ltd Device and method for methane fermentation treatment
JP2003320394A (en) * 2002-04-30 2003-11-11 Kurita Water Ind Ltd Treatment apparatus and treatment method for organic waste
JP2004160406A (en) * 2002-11-14 2004-06-10 Hokoku Kogyo Co Ltd Ammonia concentration automatic control method in biogas conversion and treatment apparatus for organic waste using the same
JP2004230273A (en) * 2003-01-30 2004-08-19 Mitsubishi Kakoki Kaisha Ltd Method for treating organic waste
JP2004249233A (en) * 2003-02-21 2004-09-09 Mitsubishi Kakoki Kaisha Ltd Method for treating organic waste

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2011071013A1 (en) * 2009-12-09 2011-06-16 メタウォーター株式会社 Methane fermentation method and methane fermentation device
JP2011120975A (en) * 2009-12-09 2011-06-23 Metawater Co Ltd Method and apparatus for methane fermentation
JP2011143326A (en) * 2010-01-12 2011-07-28 Takuma Co Ltd Dry type methane fermentation residue dehydration system
WO2014093799A1 (en) * 2012-12-14 2014-06-19 Bp Corporation North America Inc. Process for the conversion of cellulosic feedstock materials
WO2014093797A1 (en) * 2012-12-14 2014-06-19 Bp Corporation North America Inc. A sequential fermentation of hydrolysate and solids from a dilute acid hydrolysis of biomass to produce fermentation products
KR102023639B1 (en) * 2018-11-30 2019-09-20 주식회사 환경에너지오앤엠 High-rate dry anaerobic digestion apparatus for treatment of high concentration organic wastes
WO2020111747A1 (en) * 2018-11-30 2020-06-04 주식회사 환경에너지오앤엠 High rate dry-type anaerobic digestion apparatus for processing high concentration organic waste

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