JP6887556B1 - Hydrothermal treatment system - Google Patents

Hydrothermal treatment system Download PDF

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JP6887556B1
JP6887556B1 JP2020210989A JP2020210989A JP6887556B1 JP 6887556 B1 JP6887556 B1 JP 6887556B1 JP 2020210989 A JP2020210989 A JP 2020210989A JP 2020210989 A JP2020210989 A JP 2020210989A JP 6887556 B1 JP6887556 B1 JP 6887556B1
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フラビアヌス ハルディ
フラビアヌス ハルディ
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Mitsubishi Heavy Industries Environmental and Chemical Engineering Co Ltd
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Priority to PCT/JP2021/045318 priority patent/WO2022138201A1/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/60Biochemical treatment, e.g. by using enzymes
    • B09B3/65Anaerobic treatment
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/70Chemical treatment, e.g. pH adjustment or oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • C02F11/04Anaerobic treatment; Production of methane by such processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/06Treatment of sludge; Devices therefor by oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/06Treatment of sludge; Devices therefor by oxidation
    • C02F11/08Wet air oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • C02F11/125Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using screw filters
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • C02F11/126Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using drum filters
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B2101/00Type of solid waste
    • 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

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
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  • Molecular Biology (AREA)
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  • General Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Treatment Of Sludge (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

【課題】安定的にガスを生成する。【解決手段】水熱処理システム1は、有機物含有廃棄物を水熱反応させる水熱処理装置10と、水熱反応された水熱処理物を加湿する調整槽11と、加湿された水熱処理物を移送する第一移送装置21と、移送された水熱処理物を加圧して水熱処理液と残余物とに分離する加圧分離装置12と、分離された水熱処理液を貯留して加温する可溶化槽13と、加温され且つ可溶化された水熱処理液を調整槽11に返送する第二移送装置22と、可溶化槽13に貯留された水熱処理液を用いてメタンガスと消化液を生成するメタン発酵装置14と、消化液を脱水汚泥と脱水分離液に分離する脱水機15と、脱水分離液を硝化及び脱窒素して再利用水を生成する廃液処理装置16とを有する。第二移送装置22は、可溶化槽13に貯留された水熱処理液に含まれる有機物の濃度が所定濃度の場合に、メタン発酵装置14に水熱処理液を移送する。【選択図】図1PROBLEM TO BE SOLVED: To stably generate gas. SOLUTION: A hydrothermal treatment system 1 transfers a hydrothermal treatment apparatus 10 for hydrothermally reacting organic matter-containing waste, an adjusting tank 11 for humidifying the hydrothermally reacted hydrothermally treated product, and a humidified hydrothermally treated product. The first transfer device 21, the pressure separation device 12 that pressurizes the transferred hydrothermally treated product to separate it into the hydrothermally treated liquid and the residue, and the solubilization tank that stores and heats the separated hydrothermally treated product. 13 and a second transfer device 22 that returns the heated and solubilized hydrothermal treatment liquid to the adjusting tank 11, and methane that produces methane gas and digestive juice using the hydrothermal treatment liquid stored in the solubilization tank 13. It has a fermentation apparatus 14, a dehydrator 15 that separates digestive juice into dehydrated sludge and a dehydration separation liquid, and a waste liquid treatment apparatus 16 that nitrifies and denitrifies the dehydration separation liquid to generate recycled water. The second transfer device 22 transfers the hydrothermal treatment solution to the methane fermentation apparatus 14 when the concentration of the organic matter contained in the hydrothermal treatment solution stored in the solubilization tank 13 is a predetermined concentration. [Selection diagram] Fig. 1

Description

本発明は、有機物含有廃棄物からメタンガスを生成する水熱処理システムに関する。 The present invention relates to a hydrothermal treatment system that produces methane gas from organic matter-containing waste.

都市ごみなどの家庭から排出される厨芥(生ごみ)、紙や草木などの木質系廃棄物、家畜糞尿、汚泥といった有機物含有廃棄物を高温高圧の水蒸気で水熱反応させて可溶化(水熱処理)し、水熱処理された有機物含有廃棄物(水熱処理物)から溶液やスラリー等の液体(水熱処理液)を分離し、当該液体を用いて微生物や菌によるガス生成、例えば、メタン発酵を行うシステムが開発されている(例えば特許文献1、2)。水熱処理物から膵液処理液を分離するために、このシステムでは、例えばスクリーンや、特許文献3に記載されているようなスクリュープレスを使用可能である。 Solubilization (hydrothermal treatment) of kitchen waste (garbage) discharged from households such as municipal waste, woody waste such as paper and vegetation, and organic waste such as livestock manure and sludge is hydrothermally reacted with high temperature and high pressure steam. ), A liquid (hydrothermal heat treatment liquid) such as a solution or slurry is separated from the hydrothermally treated organic substance-containing waste (hydro heat treatment product), and the liquid is used to generate gas by microorganisms or bacteria, for example, methane fermentation. Systems have been developed (eg, Patent Documents 1 and 2). In order to separate the pancreatic juice treatment from the hydrothermally treated product, for example, a screen or a screw press as described in Patent Document 3 can be used in this system.

特開2009−119378号公報JP-A-2009-119378 特開2019−181397号公報Japanese Unexamined Patent Publication No. 2019-181397 特開2011−200836号公報Japanese Unexamined Patent Publication No. 2011-200836

一般的に、ゴミ収集車で回収される有機物含有廃棄物やごみ清掃工場のごみピットに貯留された有機物含有廃棄物には、ガス発生に寄与する有機物の他に、ガス発生に寄与しない又は寄与しづらい有機物(例えばプラスチック)や、金属やガラス等の無機物も完全には除去されずに残留している。また、地域、季節、日時によっても、回収され又は貯留された有機物含有廃棄物に含まれる有機物と無機物の比率や、有機物であっても厨芥と紙の比率や、ガス発生に寄与する有機物とほとんど寄与しない有機物との比率など(すなわち、所定量の有機物含有廃棄物に占める複数の内容物の各々の比率)が異なる。 In general, organic matter-containing waste collected by garbage trucks and organic matter-containing waste stored in the garbage pits of garbage trucks do not contribute to or contribute to gas generation in addition to organic matter that contributes to gas generation. Hard-to-difficult organic substances (for example, plastic) and inorganic substances such as metal and glass are not completely removed and remain. Also, depending on the region, season, and date and time, the ratio of organic matter to inorganic matter contained in the collected or stored organic matter-containing waste, the ratio of organic matter to paper even if it is organic matter, and most of the organic matter that contributes to gas generation. The ratio to non-contributory organic matter and the like (that is, the ratio of each of the plurality of contents to the predetermined amount of organic matter-containing waste) are different.

また、一般的に、有機物含有廃棄物に占める各内容物の比率がどのようなものであっても、水熱処理装置では所定量の有機物含有廃棄物が、予め定められた一定の時間(所定時間)だけ水熱処理され、当該所定時間が終了し次第、水熱処理を終了し、水熱処理装置から水熱処理物が取り出される。このため、有機物含有廃棄物に占める各内容物の比率によって、取り出される水熱処理物の性状が異なる。例えば、水分が少なく砂状または粉末状の水熱処理物が得られる場合もあれば、水分が多く泥状または液状の水熱処理物が得られる場合もある。 Further, in general, regardless of the ratio of each content to the organic matter-containing waste, a predetermined amount of the organic matter-containing waste is discharged in a predetermined amount for a predetermined time (predetermined time) in the hydrothermal treatment apparatus. ) Is hydrothermally treated, and as soon as the predetermined time is completed, the hydrothermal treatment is completed and the hydrothermally treated product is taken out from the hydrothermal treatment apparatus. Therefore, the properties of the hydrothermally treated product to be taken out differ depending on the ratio of each content to the organic matter-containing waste. For example, a sandy or powdery hydrothermally treated product having a low water content may be obtained, or a muddy or liquid hydrothermally treated product having a high water content may be obtained.

一方で、水熱処理液を用いてメタン発酵することでメタンガスを生成する場合、水熱処理物に含まれる微細な有機物が、水熱処理液に可能な限り多く含有していることが望ましい。このため、特許文献3に記載されているように、水熱処理物から水熱処理液を分離する際に、加圧式のスクリュープレスを使用するのが好適である。しかし、低水分量(例えば、砂状)の水熱処理物をスクリュープレスで加圧することは電力消費量を増大させ、また、故障を誘発する恐れがあるので好ましくない。 On the other hand, when methane gas is produced by methane fermentation using a hydrothermal treatment solution, it is desirable that the hydrothermal treatment solution contains as much fine organic matter as possible. Therefore, as described in Patent Document 3, it is preferable to use a pressure type screw press when separating the hydrothermal treatment liquid from the hydrothermal treatment product. However, pressurizing a hydrothermally treated product having a low water content (for example, sandy) with a screw press is not preferable because it increases power consumption and may induce a failure.

さらに、水熱処理液を用いてメタンガスを生成する場合、水熱処理液に含有される微細な有機物の濃度はガス生成効率を上げるために重要な要素である。しかし、当該有機物の濃度が、水分の多い水熱処理物と水分の少ない水熱処理物とでは大きく異なるため、メタン発酵装置において、安定的にガスを生成することが困難であった。 Further, when methane gas is produced using the hydrothermal treatment solution, the concentration of fine organic substances contained in the hydrothermal treatment solution is an important factor for increasing the gas generation efficiency. However, since the concentration of the organic matter is significantly different between the hydrothermally treated product having a high water content and the hydrothermally treated product having a low water content, it has been difficult to stably generate gas in the methane fermentation apparatus.

そこで、本発明では、有機物含有廃棄物に含まれる内容物の比率によらず、安定的にメタンガスを生成できる水熱処理システムを提供することを目的とする。 Therefore, an object of the present invention is to provide a hydrothermal treatment system capable of stably generating methane gas regardless of the ratio of the contents contained in the organic matter-containing waste.

本発明の水熱処理システムは、有機物含有廃棄物を水熱反応させる水熱処理装置と、前記水熱反応された水熱処理物を加湿する調整槽と、前記調整槽で加湿された水熱処理物を移送する第一移送装置と、前記第一移送装置で移送された水熱処理物を加圧して水熱処理液と残余物とに分離する加圧分離装置と、前記加圧分離装置で分離された水熱処理液を貯留して加温する可溶化槽と、前記可溶化槽で加温され且つ可溶化された水熱処理液を前記調整槽に返送する第二移送装置と、前記可溶化槽に貯留された水熱処理液を用いてメタンガスと消化液を生成するメタン発酵装置と、前記消化液を脱水汚泥と脱水分離液に分離する脱水機と、前記脱水分離液を少なくとも硝化及び脱窒素して再利用水を生成する廃液処理装置とを有し、前記第二移送装置は、前記可溶化槽に貯留された水熱処理液に含まれる有機物の濃度が微生物または菌によるメタンガスの生成に適した有機物の濃度である所定濃度未満の場合に、前記調整槽に前記水熱処理液を返送し、前記有機物の濃度が前記所定濃度以上の場合に、前記メタン発酵装置に前記水熱処理液を移送する。 In the hydrothermal treatment system of the present invention, a hydrothermal treatment apparatus for hydrothermally reacting organic matter-containing waste, an adjusting tank for humidifying the hydrothermally reacted hydrothermally-reacted product, and a hydrothermally treated product humidified in the adjusting tank are transferred. The first transfer device, the pressure separation device that pressurizes the hydrothermally treated product transferred by the first transfer device and separates it into the hydrothermal treatment liquid and the residue, and the hydrothermal treatment separated by the pressure separation device. A solubilization tank for storing and heating the liquid, a second transfer device for returning the hydrothermal treatment liquid heated and solubilized in the solubilization tank to the adjustment tank, and storage in the solubilization tank. A methane fermentation device that produces methane gas and digestive juice using a hydrothermal treatment liquid, a dehydrator that separates the digestive juice into dehydrated sludge and dehydration separation liquid, and at least nitrification and denitrification of the dehydration separation liquid to reuse water. In the second transfer device, the concentration of the organic substance contained in the hydrothermal solution stored in the solubilization tank is the concentration of the organic substance suitable for the production of methane gas by microorganisms or bacteria. When the concentration is less than a certain predetermined concentration, the hydrothermal solution is returned to the adjusting tank, and when the concentration of the organic substance is equal to or more than the predetermined concentration , the hydrothermal solution is transferred to the methane fermentation apparatus.

本発明によれば、有機物含有廃棄物に含まれる各内容物の比率によらず、安定的にメタンガスを生成することができる。 According to the present invention, methane gas can be stably generated regardless of the ratio of each content contained in the organic matter-containing waste.

実施形態に係る水熱処理システムを示す模式図である。It is a schematic diagram which shows the hydrothermal treatment system which concerns on embodiment. 実施形態に係る水熱処理システムの第二設備の一例を示す模式図である。It is a schematic diagram which shows an example of the 2nd equipment of the hydrothermal treatment system which concerns on embodiment.

以下、図面を参照して、本発明の水熱処理システムについて説明する。以下に示す構成等はあくまでも例示に過ぎず、明示しない種々の変形や技術の適用を排除する意図はない。以下に示す構成等は、本発明における必須の構成要件及びその趣旨を逸脱しない範囲で種々変形して実施することができる。 Hereinafter, the hydrothermal treatment system of the present invention will be described with reference to the drawings. The configurations shown below are merely examples, and there is no intention to exclude the application of various modifications and techniques that are not specified. The configurations and the like shown below can be variously modified and implemented without departing from the essential constituent requirements and the gist of the present invention.

図1は、本実施形態の水熱処理システム1を示す模式図である。水熱処理システム1は、有機物含有廃棄物を高温高圧の水蒸気で水熱反応させて可溶化(以下「水熱処理」という)し、水熱処理された有機物含有廃棄物(以下「水熱処理物」という)から分離される溶液、混合液、またはスラリー等の液体(以下「水熱処理液」という)を用いて、微生物や菌によるガス生成を行うシステムである。
水熱処理システム1は、水熱処理装置10と、調整槽11と、第一移送装置21と、加圧分離装置12と、可溶化槽13と、第二移送装置22と、メタン発酵装置14と、脱水機15と、廃液処理装置16とを、少なくとも含んで構成される。
では、図1に示す水熱処理システム1の全ての構成につき、以下に詳述する。
FIG. 1 is a schematic view showing the hydrothermal treatment system 1 of the present embodiment. The hydrothermal treatment system 1 solubilizes the organic matter-containing waste by hydrothermally reacting it with high-temperature and high-pressure steam (hereinafter referred to as "hydrothermal treatment"), and hydrothermally heat-treats the organic matter-containing waste (hereinafter referred to as "hydrothermal treatment product"). It is a system that generates gas by microorganisms and bacteria using a liquid (hereinafter referred to as "hydrothermal heat treatment liquid") such as a solution, a mixed liquid, or a slurry separated from the water vapor.
The water heat treatment system 1 includes a water heat treatment device 10, a adjusting tank 11, a first transfer device 21, a pressure separation device 12, a solubilization tank 13, a second transfer device 22, a methane fermentation device 14, and the like. The dehydrator 15 and the waste liquid treatment device 16 are included at least.
Then, all the configurations of the hydrothermal treatment system 1 shown in FIG. 1 will be described in detail below.

水熱処理装置10は、有機物含有廃棄物を水熱処理する装置である。水熱処理装置10に投入される有機物含有廃棄物としては、家庭から排出される厨芥(生ごみ)、木質系廃棄物、家畜糞尿、汚泥などが挙げられる。ごみ収集車で回収された有機物含有廃棄物やごみ清掃工場のごみピットに貯留された有機物含有廃棄物をそのまま水熱処理装置10に投入してもよいし、これらの有機物含有廃棄物から無機物を取り除いた後、水熱処理装置10に投入してもよい。これらの有機物含有廃棄物の中から、ガス生成に適した有機物を含有する厨芥類、紙類、草木類を選択的に取り出し、取り出した厨芥類、紙類または草木類を水熱処理装置10に投入してもよい。水熱処理装置10は、近年、高齢者施設等で処分の問題が生じている紙おむつも水熱処理することができる。
後程明らかになるが、水熱処理システム1においては、水熱処理装置10が1回の水熱処理で取り扱う所定量の有機物含有廃棄物に占める各々の内容物の比率が、複数回実施される各々の水熱処理で取り扱うそれぞれの有機物含有廃棄物ごとに大きく異なっていても、後述のメタン発酵装置14で安定的にメタンガス(バイオガス)を生成することができる。
水熱処理装置10で所定時間の水熱処理が行われ、水熱処理装置10から排出された水熱処理物は、調整槽11に貯留される。
The hydrothermal treatment apparatus 10 is an apparatus for hydrothermally treating organic matter-containing waste. Examples of the organic matter-containing waste charged into the hydrothermal treatment apparatus 10 include kitchen waste (food waste) discharged from home, wood-based waste, livestock manure, sludge and the like. The organic matter-containing waste collected by the garbage truck or the organic matter-containing waste stored in the garbage pit of the garbage truck may be directly put into the hydrothermal treatment apparatus 10, or the inorganic matter is removed from these organic matter-containing wastes. After that, it may be put into the hydrothermal treatment apparatus 10. From these organic matter-containing wastes, kitchens, papers, and plants containing organic matter suitable for gas generation are selectively taken out, and the taken out kitchens, papers, and plants are put into the hydrothermal treatment apparatus 10. You may. The hydroheat treatment apparatus 10 can hydroheat treat disposable diapers, which have recently had a problem of disposal in facilities for the elderly and the like.
As will be clarified later, in the hydrothermal treatment system 1, the ratio of each content to the predetermined amount of organic matter-containing waste handled by the hydrothermal treatment apparatus 10 in one hydrothermal treatment is determined a plurality of times for each water. Methane gas (biogas) can be stably produced by the methane fermentation apparatus 14 described later, even if the wastes containing organic substances handled by the heat treatment differ greatly.
The hydrothermal treatment apparatus 10 performs hydrothermal treatment for a predetermined time, and the hydrothermally treated product discharged from the hydrothermal treatment apparatus 10 is stored in the adjusting tank 11.

調整槽11は、水熱処理装置10から排出された水熱処理物を加湿して、水熱処理物の性状を調整する装置である。なお、ここでは、水熱処理物を「加湿」するとは、水熱処理物を水や液体で湿らせる意味のほか、水熱処理物を水や液体に浸す意味も含む。
調整槽11には、後述する可溶化槽13に貯留された水熱処理液が注液されるので、調整槽11に貯留された水熱処理物が加湿される。調整槽11には、当該水熱処理液に加え、適宜、水道水(図示省略)や後述の再利用水を注水してもよい。
また、調整槽11に撹拌装置を設置し、調整槽11に貯留された水熱処理物と、注液または注水されるこれらの液または水とを攪拌して混合してもよい。撹拌装置を設置した場合は、調整槽11は、短時間で水熱処理物の性状を調整することができる。例えば、調整槽11に貯留された水熱処理物が砂状であった場合、上記注液または上記注水を行いつつ撹拌装置を動作させることにより、当該水熱処理物を短時間でスラリー状に変化させることができる。
撹拌装置は、空気撹拌や機械撹拌など、調整槽11に貯留された水熱処理物と、注液または注水されるこれらの液または水とを攪拌して混合する装置であれば、いかような装置であってもよい。
The adjusting tank 11 is an apparatus for adjusting the properties of the hydrothermally treated product by humidifying the hydrothermally treated product discharged from the hydrothermally treated product 10. Here, "humidifying" the hydroheat-treated product includes not only the meaning of moistening the hydro-heat-treated product with water or liquid, but also the meaning of immersing the hydro-heat-treated product in water or liquid.
Since the hydrothermal treatment solution stored in the solubilization tank 13 described later is injected into the adjustment tank 11, the hydrothermal treatment product stored in the adjustment tank 11 is humidified. In addition to the hydrothermal treatment liquid, tap water (not shown) or recycled water described later may be appropriately injected into the adjusting tank 11.
Further, a stirring device may be installed in the adjusting tank 11 to stir and mix the hydrothermally treated product stored in the adjusting tank 11 with the liquid or water to be injected. When the stirring device is installed, the adjusting tank 11 can adjust the properties of the hydrothermally treated product in a short time. For example, when the hydrothermally treated product stored in the adjusting tank 11 is sandy, the hydrothermally treated product is changed into a slurry in a short time by operating the stirring device while performing the above-mentioned liquid injection or the above-mentioned water injection. be able to.
The stirring device can be any device as long as it is a device such as air stirring or mechanical stirring that stirs and mixes the hydrothermally treated product stored in the adjusting tank 11 and these liquids or water to be injected or injected. It may be.

なお、水熱処理装置10及び調整槽11は、有機物含有廃棄物を水熱処理し、且つ、水熱処理して得られた水熱処理物に加湿して貯留する設備であり、水熱処理システム1における第一段階の処理を行う第一設備2の構成要素である。
また、後述するが、第一設備2で貯留された水熱処理物を加圧して水熱処理液を分離(以下「加圧分離」という)し、当該加圧分離により得られた水熱処理液を可溶化する設備は、水熱処理システム1における第二段階の処理を行う第二設備3である。さらに、第二設備3で可溶化された水熱処理液を用いてガス生成する設備は、水熱処理システム1における第三段階の処理を行う第三設備4である。
The hydrothermal treatment apparatus 10 and the adjusting tank 11 are equipment for hydrothermally treating organic matter-containing waste and humidifying and storing the hydrothermally treated product obtained by hydrothermal treatment, and are the first in the hydrothermal treatment system 1. It is a component of the first equipment 2 that performs step processing.
Further, as will be described later, the hydrothermal treatment liquid stored in the first facility 2 is pressurized to separate the hydrothermal treatment liquid (hereinafter referred to as “pressurization separation”), and the hydrothermal treatment liquid obtained by the pressure separation can be used. The equipment to be melted is the second equipment 3 that performs the second stage treatment in the hydrothermal treatment system 1. Further, the equipment that generates gas using the hydrothermal treatment liquid solubilized in the second equipment 3 is the third equipment 4 that performs the third stage treatment in the hydrothermal treatment system 1.

第一移送装置21は、第一設備2の調整槽11で加湿された水熱処理物を第二設備3へ移送する装置である。第一設備2と第二設備3とが互いに近接して設置されている場合、例えば、第一設備2と第二設備3との距離が約500m未満である同一または近隣の敷地に設置されている場合、第一移送装置21は、第一設備2の調整槽11と第二設備3の加圧分離装置12とに接続し、且つ、調整槽11で性状が調整された水熱処理物を加圧分離装置12へ圧送する破砕ポンプを備えたパイプラインが望ましい。パイプラインは、一般的に、一つの経路を形成するよう複数の配管が接続されて構成される。
この場合は、パイプラインを通じて、第一設備2の調整槽11に貯留された水熱処理物を、破砕ポンプにより破砕しながら第二設備3の加圧分離装置12へ移送する。水熱処理物の移送の際に、破砕ポンプで水熱処理物を細かくすることができるので、後述の加圧分離装置12(例えば、スクリュープレス)の負荷を低減できる。
The first transfer device 21 is a device that transfers the hydrothermally treated product humidified in the adjusting tank 11 of the first equipment 2 to the second equipment 3. When the first equipment 2 and the second equipment 3 are installed close to each other, for example, they are installed on the same or neighboring sites where the distance between the first equipment 2 and the second equipment 3 is less than about 500 m. If so, the first transfer device 21 is connected to the adjusting tank 11 of the first equipment 2 and the pressure separating device 12 of the second equipment 3, and a hydrothermally treated product whose properties have been adjusted in the adjusting tank 11 is added. A pipeline equipped with a crushing pump that pumps to the pressure separator 12 is desirable. A pipeline is generally constructed by connecting a plurality of pipes so as to form one path.
In this case, the hydrothermally treated product stored in the adjusting tank 11 of the first equipment 2 is transferred to the pressure separating device 12 of the second equipment 3 while being crushed by the crushing pump through the pipeline. Since the hydroheat-treated product can be finely divided by a crushing pump when the hydro-heat-treated product is transferred, the load on the pressure separation device 12 (for example, a screw press) described later can be reduced.

なお、以下、第一設備2、第二設備3、及び第三設備4のうち2つの設備が「近接」して設置されるという場合には、当該2つの設備同士の距離が約500m未満の同一または異なる敷地に設置されることを意味する。 In the following, when two of the first equipment 2, the second equipment 3, and the third equipment 4 are installed in "close proximity", the distance between the two equipment is less than about 500 m. It means that it will be installed on the same or different site.

一方、第一設備2と第二設備3とが互いに遠方に設置されている場合、第一移送装置21は、貯留タンク等を備えた自動車(例えば、バキュームカー等)が望ましい。例えば、第一設備2と第二設備3とが互いに約500m以上離れて設置されていれば、同一の敷地であっても異なる敷地であっても、これらは「遠方」に設置されているといえる。この場合は、第一設備2の調整槽11に貯留された水熱処理物を自動車に積載して、第二設備3の加圧分離装置12まで運搬し、運搬した水熱処理物を加圧分離装置12へ投入する。 On the other hand, when the first equipment 2 and the second equipment 3 are installed far from each other, the first transfer device 21 is preferably an automobile equipped with a storage tank or the like (for example, a vacuum car or the like). For example, if the first equipment 2 and the second equipment 3 are installed at a distance of about 500 m or more from each other, they are installed "far away" regardless of whether they are on the same site or on different sites. I can say. In this case, the hydrothermally treated product stored in the adjusting tank 11 of the first equipment 2 is loaded on the automobile and transported to the pressure separating device 12 of the second equipment 3, and the transported hydrothermally treated product is transported by the pressure separating device. It is thrown into 12.

ここで、自動車は、人が運転する自動車でもよいし、人ではなく人工知能(Artificial Intelligence、いわゆるAI)などのコンピュータが運転を制御する自動運転の自動車であってもよい。
また、水熱処理システム1に中央制御室を設け、監視カメラを利用して人が遠隔監視しながら、自動車の運転を制御してもよい。この場合、水熱処理システム1に含まれる設備、装置、並びに施設に監視カメラを設置すれば、中央制御室でこれらの遠隔監視をすることができ、水熱処理システム1の運転の安全性を向上することができる。
さらに、水熱処理システム1は、中央制御室で、水熱処理システム1に含まれる設備、装置、並びに施設のそれぞれの運転を制御するよう構成することもでき、AIを利用することで水熱処理システム1の運転を全自動化することも可能である。
Here, the automobile may be a vehicle driven by a person, or may be an automatically driven vehicle in which a computer such as artificial intelligence (so-called AI) controls driving instead of a person.
Further, the hydrothermal treatment system 1 may be provided with a central control room, and the driving of the automobile may be controlled while a person remotely monitors using a surveillance camera. In this case, if a surveillance camera is installed in the equipment and devices included in the hydrothermal treatment system 1 and the facility, these can be remotely monitored in the central control room, and the operational safety of the hydrothermal treatment system 1 is improved. be able to.
Further, the hydrothermal treatment system 1 can be configured to control the operation of each of the equipment, devices, and facilities included in the hydrothermal treatment system 1 in the central control room, and the hydrothermal treatment system 1 can be configured by using AI. It is also possible to fully automate the operation of.

なお、以下、第一設備2、第二設備3、及び第三設備4のうち2つの設備が「遠方」に設置されるという場合には、当該2つの設備同士の距離が約500m以上の同一または異なる敷地に設置されることを意味する。
また、以下、「自動車」という場合には、当該自動車は、人が運転する自動車であっても、当該自動運転の自動車であってもよい。当該自動車は、人が遠隔監視して運転を制御する自動車であってもよい。
Hereinafter, when two of the first equipment 2, the second equipment 3, and the third equipment 4 are installed in a "distant place", the distance between the two equipments is the same of about 500 m or more. Or it means that it will be installed on a different site.
Further, hereinafter, when the term "automobile" is used, the automobile may be a human-driven vehicle or an automatically driven vehicle. The vehicle may be a vehicle that is remotely monitored by a person to control driving.

第二設備3の加圧分離装置12は、第一設備2の調整槽11から第一移送装置21で移送された水熱処理物を加圧して、水熱処理液と残余物(水熱処理物から水熱処理液が分離されて残った物)とに分離する装置である。なお、水熱処理液は発酵適物、残余物は発酵不適物ともいわれる。
加圧分離装置12は、例えば、図2に示すように、前段に回転式ドラムスクリーン12Aを配置し、後段にスクリュープレス12Bを配置した構成とすることができる。回転式ドラムスクリーン12Aは、例えば、三菱重工環境・化学エンジニアリング株式会社の特許第6384015号の登録公報に記載のパンチングメタルドラムスクリーン装置であってもよい。また、スクリュープレス12Bは、例えば、三菱重工環境・化学エンジニアリング株式会社の特許第6734496号の登録公報の図13に記載の脱水システムであってもよい。
加圧分離装置12は、水熱処理物の含水率や粘性等により、水熱処理液の回収率や発酵不適物の除去率に影響があるため、目開きや開口率、スクリューピッチ(スクリューと排出口との距離)などが慎重に設定される。上記特許第6734496号の登録公報の図13に記載の脱水システムは、水熱処理物の性状の変化に対応して目開きを変更するので、加圧分離装置12に好適である。加圧分離装置12は、水熱処理物の性状の変化に対応して、例えば、排出口の大きさを増減させて、装置内の圧力を変更してもよい。
また、加圧分離装置12は、図2と異なり、スクリュープレスのみの単体で構成してもよい。
The pressure separating device 12 of the second equipment 3 pressurizes the hydroheat-treated product transferred from the adjusting tank 11 of the first equipment 2 by the first transfer device 21, and the hydrothermal treatment liquid and the residue (water from the hydro-heat-treated product to water). It is a device that separates the heat treatment liquid into the one that remains after being separated. The hydrothermal treatment liquid is also called a fermentation-suitable product, and the residue is also called a fermentation-unsuitable product.
As shown in FIG. 2, the pressure separating device 12 may have a configuration in which the rotary drum screen 12A is arranged in the front stage and the screw press 12B is arranged in the rear stage, for example. The rotary drum screen 12A may be, for example, the punching metal drum screen device described in the registration publication of Japanese Patent No. 6384015 of Mitsubishi Heavy Industries Environmental & Chemical Engineering Co., Ltd. Further, the screw press 12B may be, for example, the dehydration system described in FIG. 13 of the registration publication of Japanese Patent No. 6734496 of Mitsubishi Heavy Industries Environmental & Chemical Engineering Co., Ltd.
Since the pressure separation device 12 affects the recovery rate of the hydroheat treatment liquid and the removal rate of unsuitable fermentation substances depending on the water content and viscosity of the hydrothermally treated product, the opening ratio, the opening ratio, and the screw pitch (screw and discharge port). Distance with) etc. are set carefully. The dehydration system described in FIG. 13 of the registration publication of Japanese Patent No. 6734496 is suitable for the pressure separation device 12 because the opening is changed in response to a change in the properties of the hydrothermally treated product. The pressure separating device 12 may change the pressure in the device by increasing or decreasing the size of the discharge port in response to the change in the properties of the hydrothermally treated product.
Further, unlike FIG. 2, the pressure separating device 12 may be configured by a single screw press only.

図2の加圧分離装置12では、第一設備2の調整槽11から第一移送装置21で移送された水熱処理物は、まず、回転式ドラムスクリーン12Aに投入される。そして、回転式ドラムスクリーン12Aで、水熱処理物から一部の水熱処理液が分離される。その後、回転式ドラムスクリーン12Aから排出された水熱処理物は、スクリュープレス12Bに投入される。
従って、前段に回転式ドラムスクリーン12Aを配置しない場合(加圧分離装置12がスクリュープレスのみの単体の場合)に比べ、後段のスクリュープレス12Bは、第一移送装置21で移送された水熱処理物の総量よりも減量した水熱処理物を加圧して水熱処理液と残余物に分離する。このため、図2の加圧分離装置12は、スクリュープレス12Bの動力低減(電力の省力化)が可能である。
なお、回転式ドラムスクリーン12Aで分離された一部の水熱処理液と、スクリュープレス12Bで分離された水熱処理液とは、いずれも第二設備3の可溶化槽13に貯留される。
In the pressure separating device 12 of FIG. 2, the hydrothermally treated product transferred from the adjusting tank 11 of the first equipment 2 by the first transfer device 21 is first charged into the rotary drum screen 12A. Then, on the rotary drum screen 12A, a part of the hydrothermal treatment liquid is separated from the hydrothermal treatment product. After that, the hydrothermally treated product discharged from the rotary drum screen 12A is charged into the screw press 12B.
Therefore, compared to the case where the rotary drum screen 12A is not arranged in the front stage (when the pressure separation device 12 is a single unit with only a screw press), the screw press 12B in the rear stage is a hydrothermally treated product transferred by the first transfer device 21. The hydrothermally treated product, which is less than the total amount of the above, is pressurized and separated into the hydrothermally treated liquid and the residue. Therefore, the pressure separating device 12 of FIG. 2 can reduce the power of the screw press 12B (power saving).
A part of the hydrothermal treatment liquid separated by the rotary drum screen 12A and the hydroheat treatment liquid separated by the screw press 12B are both stored in the solubilization tank 13 of the second facility 3.

第二設備3の可溶化槽13は、加圧分離装置12で分離された水熱処理液を貯留して加温し、水熱処理液を可溶化する装置である。加温の温度は、例えば、約40℃〜60℃とすることができる。
可溶化槽13で水熱処理液を可溶化することで、水熱処理液に浮遊している不溶性の固形物(Suspended Solids、以下「SS」という)が、水熱処理液に溶解している固形物(Dissolved Solids、以下「DS」という)に変化する。このため、可溶化槽13に貯留された水熱処理液に含まれる固形物全体量(Total Solids、以下「TS」という。TS=SS+DS)に占めるSSが減少する。従って、可溶化槽13は、貯留している水熱処理液のSSを減量し、DSを増量し、酸発酵を促進する装置ともいえる。
一般的に、TSにおける有機物のDSの量が多い方が、微生物や菌によるガス生成に望ましい。可溶化槽13に貯留された水熱処理液のTS、SS、またはDSは、専用の測定装置(図示省略)で計測することができる。
また、可溶化槽13には、調整槽11と同様に、撹拌装置を設置して、可溶化槽13に貯留された水熱処理液を攪拌し、水熱処理液の可溶化を促進してもよい。
The solubilization tank 13 of the second equipment 3 is an apparatus that stores and heats the hydrothermal treatment liquid separated by the pressure separation device 12 to solubilize the hydrothermal treatment liquid. The heating temperature can be, for example, about 40 ° C to 60 ° C.
By solubilizing the hydrothermal solution in the solubilization tank 13, insoluble solids (Suspended Solids, hereinafter referred to as “SS”) suspended in the hydrothermal solution are dissolved in the hydrothermal solution (the solids (hereinafter referred to as “SS”)). It changes to Dissolved Solids (hereinafter referred to as "DS"). Therefore, SS in the total amount of solids (Total Solids, hereinafter referred to as “TS”; TS = SS + DS) contained in the hydrothermal treatment liquid stored in the solubilization tank 13 is reduced. Therefore, the solubilization tank 13 can be said to be an apparatus for reducing the amount of SS in the stored hydrothermal treatment solution, increasing the amount of DS, and promoting acid fermentation.
In general, it is desirable that the amount of organic DS in TS is large for gas production by microorganisms and fungi. The TS, SS, or DS of the hydrothermal treatment solution stored in the solubilization tank 13 can be measured with a dedicated measuring device (not shown).
Further, in the solubilization tank 13, similarly to the adjustment tank 11, a stirring device may be installed to stir the hydrothermal treatment solution stored in the solubilization tank 13 to promote the solubilization of the hydrothermal treatment solution. ..

第二移送装置22は、第二設備3の可溶化槽13に貯留された水熱処理液に含まれる有機物の濃度が所定濃度(例えば、TSが約10%、DSが約6%)未満の場合に、当該水熱処理液を可溶化槽13から第一設備2の調整槽11へ返送し、当該所定濃度に達した場合(実質的に当該所定濃度以上の場合を含む。また、当該所定濃度は、例えば、TSが約10%〜12%、DSが約6%〜8%など、範囲のある濃度であってもよい)に、当該水熱処理液を可溶化槽13から第三設備4のメタン発酵装置14に移送する装置である。
第二移送装置22は、先述の測定装置の測定結果に基づき、調整槽11とメタン発酵装置14のいずれか一方を移送先として自動的に選択し、可溶化槽13に貯留された水熱処理液を当該選択した移送先へ移送する構成としてもよい。
なお、当該所定濃度は、後述のメタン発酵装置14で、メタン発酵に適した有機物の濃度、すなわち微生物または菌によるメタンガスの生成に適した有機物の濃度に設定される。当該所定濃度においては、可溶化槽13に貯留された水熱処理液のpH値(ペーハー値)は7未満の酸性となっており、pH値が5以下であることが望ましい。
In the second transfer device 22, when the concentration of the organic substance contained in the hydrothermal treatment solution stored in the solubilization tank 13 of the second facility 3 is less than a predetermined concentration (for example, TS is about 10% and DS is about 6%). When the hydrothermal treatment solution is returned from the solubilization tank 13 to the adjustment tank 11 of the first equipment 2 and reaches the predetermined concentration (including the case where the concentration is substantially equal to or higher than the predetermined concentration), the predetermined concentration is , For example, TS may have a concentration of about 10% to 12%, DS may have a concentration of about 6% to 8%, etc.), and the hydrothermal treatment solution is mixed with the solubilization tank 13 to the methane of the third facility 4. It is an apparatus to be transferred to the fermentation apparatus 14.
The second transfer device 22 automatically selects either one of the adjusting tank 11 and the methane fermentation device 14 as the transfer destination based on the measurement results of the above-mentioned measuring device, and the hydrothermal treatment liquid stored in the solubilization tank 13. May be configured to be transferred to the selected transfer destination.
The predetermined concentration is set by the methane fermentation apparatus 14 described later to a concentration of an organic substance suitable for methane fermentation, that is, a concentration of an organic substance suitable for the production of methane gas by a microorganism or a fungus. At the predetermined concentration, the pH value (pH value) of the hydrothermal treatment solution stored in the solubilization tank 13 is less than 7, and it is desirable that the pH value is 5 or less.

第二移送装置22は、第一移送装置21と同様に、第一設備2と第二設備3とが互いに近接して設置されている場合、第一設備2の調整槽11と第二設備3の可溶化槽13とに接続し、且つ、可溶化槽13の水熱処理液を調整槽11へ圧送するポンプを備えたパイプラインが望ましい。
一方、第一設備2と第二設備3とが互いに遠方に設置されている場合、第二移送装置22は、貯留タンク等を備えた自動車(例えば、バキュームカー等)が望ましい。この場合は、自動車によって可溶化槽13から調整槽11へ水熱処理液を運搬する。
いずれの場合も、第二移送装置22により、水熱処理液は、第一設備2と第二設備3との間を循環することになる。
Similar to the first transfer device 21, the second transfer device 22 has the adjusting tank 11 and the second facility 3 of the first facility 2 when the first facility 2 and the second facility 3 are installed close to each other. A pipeline provided with a pump connected to the solubilization tank 13 and pumping the hydrothermal solution of the solubilization tank 13 to the adjustment tank 11 is desirable.
On the other hand, when the first equipment 2 and the second equipment 3 are installed far from each other, the second transfer device 22 is preferably an automobile equipped with a storage tank or the like (for example, a vacuum car or the like). In this case, the hydrothermal treatment liquid is transported from the solubilization tank 13 to the adjustment tank 11 by an automobile.
In either case, the hydrothermal treatment liquid is circulated between the first equipment 2 and the second equipment 3 by the second transfer device 22.

また、第二移送装置22は、第二設備3と第三設備4とが互いに近接して設置されている場合、第二設備3の可溶化槽13と第三設備4のメタン発酵装置14とに接続し、且つ、可溶化槽13の水熱処理液をメタン発酵装置14の投入口へ圧送するポンプを備えたパイプラインが望ましい。 Further, in the second transfer device 22, when the second facility 3 and the third facility 4 are installed close to each other, the solubilization tank 13 of the second facility 3 and the methane fermentation device 14 of the third facility 4 are installed. A pipeline having a pump that is connected to the solubilization tank 13 and pumps the hydrothermal treatment liquid of the solubilization tank 13 to the inlet of the methane fermentation apparatus 14 is desirable.

なお、第一設備2と第二設備3と第三設備4とが互いに近接して設置されている場合、第二移送装置22は、例えば、第二設備3の可溶化槽13と第一設備2の調整槽11とを接続するパイプラインの途中に切替装置を備え、当該パイプラインから分岐した別のパイプラインを、当該切替装置と第三設備4のメタン発酵装置14の投入口とに接続する構成としてもよい。
上述したように、第二設備3の可溶化槽13に貯留された水熱処理液に含まれる有機物の濃度に応じて、第二設備3の可溶化槽13と第一設備2の調整槽11とを接続するパイプラインと、上記別のパイプラインとのいずれか一方で、可溶化槽13に貯留された水熱処理液を移送するよう、第二移送装置22は、切替装置で択一的に選択することができる。
When the first equipment 2, the second equipment 3, and the third equipment 4 are installed close to each other, the second transfer device 22 may be, for example, the solubilization tank 13 and the first equipment of the second equipment 3. A switching device is provided in the middle of the pipeline connecting the adjusting tank 11 of No. 2, and another pipeline branched from the pipeline is connected to the switching device and the inlet of the methane fermentation apparatus 14 of the third facility 4. It may be configured to be used.
As described above, the solubilization tank 13 of the second equipment 3 and the adjustment tank 11 of the first equipment 2 are used according to the concentration of the organic matter contained in the hydrothermal treatment solution stored in the solubilization tank 13 of the second equipment 3. The second transfer device 22 is selectively selected by the switching device so as to transfer the hydrothermal treatment solution stored in the solubilization tank 13 to one of the pipeline connecting the above and the other pipeline described above. can do.

一方、第二設備3と第三設備4とが互いに遠方に設置されている場合、第二移送装置22は、貯留タンク等を備えた自動車(例えば、バキュームカー等)が望ましい。この場合は、自動車によって可溶化槽13からメタン発酵装置14へ水熱処理液を運搬し、メタン発酵装置14の投入口へ当該水熱処理液が投入される。
なお、第一設備2と第二設備3とが互いに近接して設置され、且つ、第二設備3と第三設備4とが互いに遠方に設置されている場合、第二移送装置22としては、第一設備2と第二設備3との間の水熱処理液の移送はパイプライン、また、第二設備3と第三設備4との間の水熱処理液の移送は自動車であってもよい。すなわち、第二移送装置22は、パイプラインと自動車の2種類の移送装置を兼ね備えてよい。
同様に、第一設備2と第二設備3とが互いに遠方に設置され、且つ、第二設備3と第三設備4とが互いに近接して設置されている場合、第二移送装置22としては、第一設備2と第二設備3との間の水熱処理液の移送は自動車、また、第二設備3と第三設備4との間の水熱処理液の移送はパイプラインであってもよい。
On the other hand, when the second equipment 3 and the third equipment 4 are installed far from each other, the second transfer device 22 is preferably an automobile equipped with a storage tank or the like (for example, a vacuum car or the like). In this case, the hydrothermal treatment liquid is transported from the solubilization tank 13 to the methane fermentation apparatus 14 by an automobile, and the hydrothermal treatment liquid is charged into the inlet of the methane fermentation apparatus 14.
When the first equipment 2 and the second equipment 3 are installed close to each other and the second equipment 3 and the third equipment 4 are installed far from each other, the second transfer device 22 may be used. The transfer of the hydrothermal solution between the first facility 2 and the second facility 3 may be performed by a pipeline, and the transfer of the hydrothermal solution between the second facility 3 and the third facility 4 may be performed by an automobile. That is, the second transfer device 22 may include two types of transfer devices, a pipeline and an automobile.
Similarly, when the first equipment 2 and the second equipment 3 are installed far from each other and the second equipment 3 and the third equipment 4 are installed close to each other, the second transfer device 22 may be used. The transfer of the hydrothermal solution between the first facility 2 and the second facility 3 may be performed by an automobile, and the transfer of the hydrothermal solution between the second facility 3 and the third facility 4 may be performed by a pipeline. ..

第二移送装置22は、第二設備3の可溶化槽13に貯留された水熱処理液に含まれる有機物の濃度が、上述した所定濃度になるまで、当該水熱処理液を第一設備2の調整槽11に返送する。
従って、第一設備2の調整槽11に貯留された水熱処理物を加湿することができるので、第一移送装置21による水熱処理物の移送を容易にし、第二設備3の加圧分離装置12の動力を低減することができる。
The second transfer device 22 adjusts the hydrothermal treatment solution of the first facility 2 until the concentration of the organic substance contained in the hydrothermal treatment solution stored in the solubilization tank 13 of the second facility 3 reaches the above-mentioned predetermined concentration. It will be returned to the tank 11.
Therefore, since the hydroheat-treated product stored in the adjusting tank 11 of the first equipment 2 can be humidified, the hydro-heat-treated product can be easily transferred by the first transfer device 21, and the pressure separation device 12 of the second equipment 3 can be easily transferred. Power can be reduced.

また、第二設備3の可溶化槽13から第一設備2の調整槽11へ返送される水熱処理液は、可溶化槽13で加温されているので、当該加温された温度のまま又は自然放熱等で少々冷却されたとしても常温より高い温度を維持したまま調整槽11へ注液することが可能である。
この場合、当該返送される水熱処理液は、調整槽11に貯留された水熱処理物の少なくとも一部の可溶化を促進するなどして当該水熱処理物の性状の調整に寄与することができる。
Further, since the hydrothermal treatment solution returned from the solubilization tank 13 of the second equipment 3 to the adjustment tank 11 of the first equipment 2 is heated in the solubilization tank 13, the heated temperature remains unchanged or Even if it is cooled a little by natural heat dissipation or the like, it is possible to inject liquid into the adjusting tank 11 while maintaining a temperature higher than room temperature.
In this case, the returned hydrothermal treatment liquid can contribute to the adjustment of the properties of the hydrothermal treatment product by promoting solubilization of at least a part of the hydrothermal treatment product stored in the adjusting tank 11.

その上、水熱処理システム1では、時間的に順次、複数回の水熱処理が行われるが、第一設備2の水熱処理装置10が水熱処理する有機物含有廃棄物に占める各々の内容物の比率が水熱処理のたびに大きく異なり、各水熱処理で得られる水熱処理液に含まれる有機物の濃度に大きなばらつきがあっても、上記返送により、第一設備2と第二設備3との間を水熱処理液が循環することで、可溶化槽13に貯留される水熱処理液に含まれる有機物の濃度を平均化することができる。
そして、可溶化槽13に貯留された水熱処理液に含まれる有機物の濃度が所定濃度になった場合、当該所定濃度の水熱処理液が第二移送装置22によりメタン発酵装置14に移送される。このため、メタン発酵装置14に投入される水熱処理液に含まれる有機物の濃度は実質的に常に一定でばらつきが少なく、且つ、当該水熱処理液はメタンガスの発生に寄与する有機物を多く含有している。従って、メタン発酵装置14は安定的にメタンガスを生成することができる。
In addition, in the hydrothermal treatment system 1, a plurality of hydrothermal treatments are sequentially performed in time, and the ratio of each content to the organic matter-containing waste to be hydrothermally treated by the hydrothermal treatment apparatus 10 of the first facility 2 is Even if the concentration of organic substances contained in the hydrothermal solution obtained by each hydrothermal treatment varies greatly depending on the hydrothermal treatment, the hydrothermal treatment between the first equipment 2 and the second equipment 3 is performed by the above return. By circulating the liquid, the concentration of the organic substance contained in the hydrothermal treatment liquid stored in the solubilization tank 13 can be averaged.
Then, when the concentration of the organic substance contained in the hydrothermal treatment solution stored in the solubilization tank 13 reaches a predetermined concentration, the hydrothermal treatment solution having the predetermined concentration is transferred to the methane fermentation apparatus 14 by the second transfer device 22. Therefore, the concentration of the organic matter contained in the hydrothermal treatment liquid charged into the methane fermentation apparatus 14 is substantially always constant and has little variation, and the hydrothermal treatment liquid contains a large amount of organic matter that contributes to the generation of methane gas. There is. Therefore, the methane fermentation apparatus 14 can stably generate methane gas.

有機物を原料として微生物や菌によりメタンガスを生成するメタン発酵装置では、一般的に、その装置内部で、まず、有機物の可溶化と酸発酵の2つの工程を行う必要がある。
しかし、水熱処理システム1では、可溶化槽13に貯留された水熱処理液に含まれる有機物の濃度が当該所定濃度になった場合、可溶化槽13において、既に上記2つの工程が実行され且つ完了している。従って、メタン発酵装置14は、可溶化の工程と酸発酵の工程を省略できるので、高速にメタンガスを生成することができる。
In a methane fermentation apparatus that produces methane gas by microorganisms or bacteria using organic matter as a raw material, it is generally necessary to first perform two steps of solubilization of the organic matter and acid fermentation inside the apparatus.
However, in the hydrothermal treatment system 1, when the concentration of the organic substance contained in the hydrothermal treatment solution stored in the solubilization tank 13 reaches the predetermined concentration, the above two steps are already executed and completed in the solubilization tank 13. doing. Therefore, since the methane fermentation apparatus 14 can omit the solubilization step and the acid fermentation step, methane gas can be generated at high speed.

第三設備4のメタン発酵装置14は、第二設備3の可溶化槽13に貯留された水熱処理液を用いてメタンガスと消化液を生成する装置である。メタン発酵装置14は、当該水熱処理液を加温(約37℃もしくは約55℃)し、メタン発酵によりメタンガスを生成する。メタンガスの生成後に残る液肥(発酵残渣、消化汚泥とも呼ばれる)が消化液である。
第二設備3の可溶化槽13に貯留された水熱処理液に、例えば紙類の繊維分が多く含まれる場合、当該繊維分は、メタン発酵装置14で完全には分解されず一部残留し、消化液に含有されて排出される。従って、消化液に繊維分が十分に含まれている場合は、後述の脱水機15の脱水効率を向上する目的で、後述の解繊液供給装置17や後述のし尿受入槽18を設ける必要はない。
The methane fermentation apparatus 14 of the third facility 4 is an apparatus that produces methane gas and digestive juice using the hydrothermal treatment liquid stored in the solubilization tank 13 of the second facility 3. The methane fermentation apparatus 14 heats the hydrothermal treatment liquid (about 37 ° C. or about 55 ° C.) and produces methane gas by methane fermentation. The liquid fertilizer (fermentation residue, also called digestive sludge) that remains after the production of methane gas is the digestive juice.
When, for example, a large amount of paper fibers is contained in the hydrothermal treatment solution stored in the solubilization tank 13 of the second facility 3, the fibers are not completely decomposed by the methane fermentation apparatus 14 and partially remain. , Contained in digestive juices and excreted. Therefore, when the digestive juice contains a sufficient amount of fiber, it is necessary to provide the defibrating liquid supply device 17 described later and the human waste receiving tank 18 described later for the purpose of improving the dehydration efficiency of the dehydrator 15 described later. Absent.

脱水機15は、メタン発酵装置14から排出される消化液を、脱水汚泥と脱水分離液に分離する装置(例えば、スクリュープレス)である。分離された脱水汚泥は、後述する廃棄物焼却施設20へ移送され、廃棄物焼却施設20において焼却処分することができる。一方、分離された脱水分離液は、廃液処理装置16へ移送される。 The dehydrator 15 is an apparatus (for example, a screw press) that separates the digested liquid discharged from the methane fermentation apparatus 14 into dehydrated sludge and dehydrated separated liquid. The separated dehydrated sludge is transferred to the waste incinerator 20 described later, and can be incinerated at the waste incinerator 20. On the other hand, the separated dehydration separation liquid is transferred to the waste liquid treatment device 16.

廃液処理装置16は、脱水機15で分離された脱水分離液に対して少なくとも硝化及び脱窒素の処理、すなわち生物処理をして脱水分離液を浄化し、再利用水を生成する装置である。廃液処理装置16としては、例えば、硝化及び脱窒素の処理を行う生物処理装置やし尿処理施設が挙げられる。
廃液処理装置16で生成された再利用水は、供給路25(例えば、パイプライン)を通じて第一設備2の調整槽11に供給することができる。
水熱処理システム1の運転開始直後は、第二設備3の可溶化槽13に水熱処理液が貯留されていないため、水熱処理システム1は当該水熱処理液を調整槽11に返送することができず、当該水熱処理液で調整槽11に貯留された水熱処理物を加湿することができない。そこで、この場合に、水熱処理システム1は、再利用水を廃液処理装置16から調整槽11に供給することで、調整槽11に貯留された水熱処理物を加湿することができ、水熱処理システム1の運転開始直後から第一移送装置21による水熱処理物の移送や第二設備3の加圧分離装置12の運転を円滑に行うことができる。
上述の返送ができない場合に、水熱処理システム1は、水道水を調整槽11に注水して水熱処理物を加湿することもできる。しかし、水熱処理システム1のコストパフォーマンスを良好にするために、水道水ではなく再利用水を使用するのが望ましい。
The waste liquid treatment device 16 is a device that purifies the dehydration separation liquid by at least nitrification and denitrification treatment, that is, biological treatment, on the dehydration separation liquid separated by the dehydrator 15, and generates recycled water. Examples of the waste liquid treatment device 16 include a biological treatment device and a urine treatment facility that perform nitrification and denitrification treatment.
The recycled water generated by the waste liquid treatment device 16 can be supplied to the adjusting tank 11 of the first facility 2 through the supply path 25 (for example, a pipeline).
Immediately after the start of operation of the hydrothermal treatment system 1, since the hydrothermal treatment liquid is not stored in the solubilization tank 13 of the second facility 3, the hydrothermal treatment system 1 cannot return the hydrothermal treatment liquid to the adjusting tank 11. , The hydrothermally treated product stored in the adjusting tank 11 cannot be humidified with the hydrothermally treated liquid. Therefore, in this case, the hydrothermal treatment system 1 can humidify the hydrothermally treated product stored in the adjusting tank 11 by supplying the recycled water from the waste liquid treatment device 16 to the adjusting tank 11. Immediately after the start of the operation of No. 1, the hydrothermally treated material can be smoothly transferred by the first transfer device 21 and the pressure separation device 12 of the second facility 3 can be smoothly operated.
When the above-mentioned return is not possible, the hydrothermal treatment system 1 can also inject tap water into the adjusting tank 11 to humidify the hydrothermally treated product. However, in order to improve the cost performance of the hydrothermal treatment system 1, it is desirable to use recycled water instead of tap water.

以上、水熱処理システム1が少なくとも備える構成について説明した。しかし、水熱処理システム1は、図1に示すように、さらに、以下の装置や施設を備えてもよい。 The configuration of at least the hydrothermal treatment system 1 has been described above. However, as shown in FIG. 1, the hydrothermal treatment system 1 may further include the following devices and facilities.

解繊液供給装置17は、紙類(例えば、古新聞などの古紙)を解繊し、液状にした解繊液を、メタン発酵装置14から排出された消化液に供給する装置である。
解繊液供給装置17が解繊液を消化液に混入するので、脱水機15では、消化液と解繊液との混合液が脱水される。解繊液には繊維分が多く含まれているため、当該混合液に含まれる繊維分が、脱水助剤の代用として機能し、上記混合液の水分を吸い取る。従って、脱水機15における当該混合液の脱水効率を向上させることができる。なお、当該繊維分は、脱水汚泥の一部として脱水機15から排出されるので、解繊液を消化液に混入しない場合に比べ、脱水汚泥の嵩が増す。
さらに、解繊液に含まれる繊維分は窒素成分を含有しておらず、また、上記混合液の水分を吸い取る際、当該混合液に含まれる窒素成分も吸い取るので、脱水機15で分離される脱水分離液中の窒素濃度が薄まる。従って、廃液処理装置16における生物処理の負荷を低減できる。解繊液供給装置17は、例えば、三菱重工環境・化学エンジニアリング株式会社の特許第5905364号の登録公報に記載の紙類供給装置、解繊装置、解繊古紙貯留タンク、及び解繊古紙供給ポンプで構成されてもよい。
The defibrating liquid supply device 17 is a device that defibrate papers (for example, used paper such as old newspapers) and supply the liquefied defibrating liquid to the digestive liquid discharged from the methane fermentation device 14.
Since the defibrating liquid supply device 17 mixes the defibrating liquid with the digested liquid, the dehydrator 15 dehydrates the mixed liquid of the digested liquid and the defibrated liquid. Since the defibrating solution contains a large amount of fiber, the fiber contained in the mixed solution functions as a substitute for the dehydration aid and absorbs the water content of the mixed solution. Therefore, the dehydration efficiency of the mixed solution in the dehydrator 15 can be improved. Since the fiber content is discharged from the dehydrator 15 as a part of the dehydrated sludge, the volume of the dehydrated sludge increases as compared with the case where the defibrating liquid is not mixed with the digestive juice.
Further, the fiber content contained in the defibrating solution does not contain a nitrogen component, and when the water content of the mixed solution is absorbed, the nitrogen component contained in the mixed solution is also absorbed, so that the fiber content is separated by the dehydrator 15. The nitrogen concentration in the dehydration separation solution diminishes. Therefore, the load of biological treatment in the waste liquid treatment device 16 can be reduced. The defibration liquid supply device 17 is, for example, a paper supply device, a defibration device, a defibration waste paper storage tank, and a defibration waste paper supply pump described in the registration publication of Japanese Patent No. 5905364 of Mitsubishi Heavy Industries Environmental & Chemical Engineering Co., Ltd. It may be composed of.

し尿受入槽18は、し尿を貯留する水槽である。水熱処理システム1では、し尿の「C/N比」(液中に含まれる窒素量と生物処理における脱窒素の際に微生物が栄養源とする炭素量の比率)が約3〜5であるという特性、及び、し尿には繊維分が含まれるという特性を利用することができる。
具体的には、水熱処理システム1では、し尿受入槽18に貯留されているし尿を、メタン発酵装置14、または、メタン発酵装置14から排出される消化液、もしくは、廃液処理装置16に供給する。なお、これら三箇所のうちの一箇所のみならず、二箇所または全てにし尿を供給してもよい。
The human waste receiving tank 18 is a water tank for storing human waste. In the hydrothermal treatment system 1, the "C / N ratio" of urine (the ratio of the amount of nitrogen contained in the liquid to the amount of carbon used as a nutrient source by microorganisms during denitrification in biological treatment) is said to be about 3 to 5. The property and the property that the urine contains fiber can be utilized.
Specifically, in the hydrothermal treatment system 1, the human waste stored in the human waste receiving tank 18 is supplied to the methane fermentation apparatus 14, the digestive juice discharged from the methane fermentation apparatus 14, or the waste liquid treatment apparatus 16. .. In addition, urine may be supplied not only to one of these three locations but also to two or all of them.

メタン発酵装置14において効率良くメタン発酵するためには、水熱処理液に含まれる窒素量が約1000mg/L以上、かつ、約3000mg/L以下である必要がある。しかし、可溶化槽13からメタン発酵装置14に移送される水熱処理液に含まれる窒素量がこれに満たない場合がありうる。
この場合、し尿受入槽18のし尿をメタン発酵装置14に供給して水熱処理液と混合することで、メタン発酵装置14に移送された水熱処理液に含まれる窒素量の不足をし尿で補うことができる。すなわち、メタン発酵の際の窒素量のバランスを整えるためにし尿を供給する。
なお、メタン発酵装置14にし尿が供給されることで、メタン発酵装置14に貯留された水熱処理液に含まれる炭素量が増加するが、メタン発酵装置14内で、炭素は大部分がメタンガスに変化するため、水熱処理システム1に悪影響を与えることはない。
また、し尿受入槽18のし尿は、メタン発酵装置14に直接的に供給されずに、メタン発酵装置14の上流、例えば、第一設備2の調整槽11や第二設備3の可溶化槽13に供給されてもよい。この場合、し尿は、メタン発酵装置14に間接的に供給される。
In order to efficiently ferment methane in the methane fermentation apparatus 14, the amount of nitrogen contained in the hydrothermal treatment solution needs to be about 1000 mg / L or more and about 3000 mg / L or less. However, the amount of nitrogen contained in the hydrothermal treatment solution transferred from the solubilization tank 13 to the methane fermentation apparatus 14 may be less than this.
In this case, by supplying the human waste from the human waste receiving tank 18 to the methane fermentation apparatus 14 and mixing it with the hydrothermal treatment solution, the amount of nitrogen contained in the hydrothermal treatment solution transferred to the methane fermentation apparatus 14 is supplemented with urine. Can be done. That is, human waste is supplied to balance the amount of nitrogen during methane fermentation.
By supplying urine to the methane fermentation apparatus 14, the amount of carbon contained in the hydrothermal treatment liquid stored in the methane fermentation apparatus 14 increases, but most of the carbon in the methane fermentation apparatus 14 becomes methane gas. Since it changes, it does not adversely affect the hydrothermal treatment system 1.
Further, the human waste in the human waste receiving tank 18 is not directly supplied to the methane fermentation apparatus 14, but is upstream of the methane fermentation apparatus 14, for example, the adjusting tank 11 of the first equipment 2 and the solubilization tank 13 of the second equipment 3. May be supplied to. In this case, human waste is indirectly supplied to the methane fermentation apparatus 14.

また、し尿受入槽18のし尿をメタン発酵装置14から排出された消化液に供給して混合液にする場合、上述した解繊液に含まれる繊維分と同様、し尿に含まれる繊維分が脱水助剤の代用として機能し、脱水機15における当該混合液の脱水効率を向上させることができる。
解繊液供給装置17とし尿受入槽18の両方を備えている水熱処理システム1であれば、消化液に含まれる繊維分が少なく上記脱水効率の向上のために繊維分を補う必要がある場合、解繊液やし尿の繊維分によってその不足分を補うことができる。なお、水熱処理システム1は、解繊液供給装置17とし尿受入槽18のいずれか一方のみを備えていてもよいし、両方を備えていてもよい。
Further, when the urine from the urine receiving tank 18 is supplied to the digestive juice discharged from the methane fermentation apparatus 14 to form a mixed solution, the fibers contained in the urine are dehydrated in the same manner as the fibers contained in the defibrating solution described above. It functions as a substitute for an auxiliary agent, and can improve the dehydration efficiency of the mixed solution in the dehydrator 15.
In the case of the hydrothermal treatment system 1 provided with both the defibration liquid supply device 17 and the urine receiving tank 18, the fiber content in the digestive juice is small and it is necessary to supplement the fiber content in order to improve the dehydration efficiency. The deficiency can be supplemented by the fiber content of the defibrating solution and palm urine. The hydrothermal treatment system 1 may be provided with only one of the defibration liquid supply device 17 and the urine receiving tank 18, or may be provided with both.

ところで、一般的に、液体の脱窒素の生物処理を行う際、当該液体のC/N比が約2〜3であると効率良く処理を行うことができる。そのため、廃液処理装置16で脱水分離液の生物処理を行う際、脱水分離液のC/N比が2未満であるときは、し尿受入槽18のし尿を脱水分離液に供給して混合することで、C/N比の値を上昇させるとよい。
脱水分離液とし尿を混合して混合液とする際、脱水分離液にし尿が追加されることで炭素量も窒素量も増加するが、上述のとおり、し尿のC/N比は約3〜5であるので、炭素量の増分の方が窒素量の増分よりも大きい。従って、脱水分離液のC/N比が2未満でも、し尿と混合することで当該混合液のC/N比を容易に約2〜3とすることができる。すなわち、ここでは、生物処理が行われる脱水分離液のC/N比のバランスを整えるためにし尿を供給する。
By the way, in general, when the biological treatment of denitrification of a liquid is performed, the treatment can be efficiently performed when the C / N ratio of the liquid is about 2 to 3. Therefore, when the biological treatment of the dehydrated separation liquid is performed by the waste liquid treatment device 16, when the C / N ratio of the dehydrated separation liquid is less than 2, the human waste from the human waste receiving tank 18 is supplied to the dehydrated separation liquid and mixed. Therefore, it is advisable to increase the value of the C / N ratio.
When urine is mixed as a dehydration-separated solution to make a mixed solution, the amount of carbon and nitrogen increases due to the addition of urine to the dehydration-separated solution, but as described above, the C / N ratio of urine is about 3 to. Since it is 5, the increase in the amount of carbon is larger than the increase in the amount of nitrogen. Therefore, even if the C / N ratio of the dehydrated separation solution is less than 2, the C / N ratio of the mixed solution can be easily set to about 2 to 3 by mixing with human waste. That is, here, human waste is supplied in order to balance the C / N ratio of the dehydrated separation liquid to which the biological treatment is performed.

第三移送装置23は、第三設備4のメタン発酵装置14で生成されたメタンガスを、後述のガス利用施設19へ移送する装置である。
メタン発酵装置14とガス利用施設19とが互いに近接して設置されている場合、第三移送装置23は、メタン発酵装置14とガス利用施設19とに接続し、且つ、メタン発酵装置14で生成したメタンガスをガス利用施設19へ移送するパイプラインが望ましい。
一方、メタン発酵装置14とガス利用施設19とが互いに遠方に設置されている場合、第三移送装置23は、ガスボンベを積載する荷台を備えた自動車(トラック)やガスタンクを搭載した自動車が望ましい。この場合は、メタン発酵装置14で生成されたメタンガスをガスボンベやガスタンクに充填して自動車に積載または搭載し、ガス利用施設19へ移送することができる。
The third transfer device 23 is a device that transfers the methane gas generated by the methane fermentation device 14 of the third facility 4 to the gas utilization facility 19 described later.
When the methane fermentation apparatus 14 and the gas utilization facility 19 are installed close to each other, the third transfer apparatus 23 is connected to the methane fermentation apparatus 14 and the gas utilization facility 19 and is generated by the methane fermentation apparatus 14. A pipeline that transfers the generated methane gas to the gas utilization facility 19 is desirable.
On the other hand, when the methane fermentation apparatus 14 and the gas utilization facility 19 are installed far from each other, the third transfer apparatus 23 is preferably an automobile (truck) equipped with a loading platform for loading a gas cylinder or an automobile equipped with a gas tank. In this case, the methane gas generated by the methane fermentation apparatus 14 can be filled in a gas cylinder or a gas tank, loaded or mounted on an automobile, and transferred to the gas utilization facility 19.

ガス利用施設19は、第三設備4のメタン発酵装置14で生成されたメタンガスを利用する施設である。ガス利用施設19は、例えば、当該メタンガスまたは当該メタンガスに他のガスを混合した混合ガスをボイラーで燃焼して生じた熱により水蒸気を生成し、この水蒸気で蒸気タービンを回すことで発電する発電プラントである。近年、火力発電所においては、燃焼時の二酸化炭素排出量を低減するため、メタンを主成分とする液化天然ガス LNG(Liquefied Natural Gas)を燃料とする火力発電所が主流になっており、ガス利用施設19も当該火力発電所に準じた発電プラントにすることができる。
ガス利用施設19は、ガスタービン、ガスエンジン、または燃料電池などを備えた発電プラントや、当該メタンガスを改質して都市ガス等を生成する施設などでもよい。
ガス利用施設19が、ガスエンジンを備えた発電プラントである場合、一般的に、ガスエンジンで生じる排ガスの熱回収装置を備えている。当該熱回収装置は、当該排ガスから温水を生成することができる。
The gas utilization facility 19 is a facility that utilizes methane gas generated by the methane fermentation apparatus 14 of the third facility 4. The gas utilization facility 19 is, for example, a power plant that generates steam by burning the methane gas or a mixed gas obtained by mixing the methane gas with another gas in a boiler to generate steam and turning a steam turbine with the steam. Is. In recent years, in order to reduce carbon dioxide emissions during combustion, thermal power plants that use methane-based liquefied natural gas LNG (Liquefied Natural Gas) as fuel have become the mainstream of thermal power plants. The facility 19 can also be a power plant similar to the thermal power plant.
The gas utilization facility 19 may be a power plant equipped with a gas turbine, a gas engine, a fuel cell, or the like, or a facility that reforms the methane gas to generate city gas or the like.
When the gas utilization facility 19 is a power plant equipped with a gas engine, it generally includes a heat recovery device for exhaust gas generated by the gas engine. The heat recovery device can generate hot water from the exhaust gas.

ガス利用施設19が蒸気タービンで発電する発電プラントであり、且つ、第一設備2と第二設備3と第三設備4の少なくともいずれか一つとガス利用施設19とが互いに近接して設置されている場合、ガス利用施設19の蒸気タービンで発電に利用された後の高温の水蒸気である廃水蒸気を当該近接している第一設備2、第二設備3、または第三設備4で利用することができる。
例えば、蒸気タービンを備えたガス利用施設19が、第一設備2に近接して設置されている場合、ガス利用施設19と第一設備2とをパイプラインで接続して、当該パイプラインを介して廃水蒸気を第一設備2の水熱処理装置10に移送し、水熱処理装置10が使用する高温高圧の水蒸気として又はその一部として利用することができる。
また、蒸気タービンを備えたガス利用施設19が、第二設備3に近接して設置されている場合、ガス利用施設19と第二設備3とをパイプラインで接続して、当該パイプラインを介して廃水蒸気を第二設備3の可溶化槽13に移送し、可溶化槽13に貯留された水熱処理液の加温に利用することができる。
さらに、蒸気タービンを備えたガス利用施設19が、第三設備4に近接して設置されている場合、ガス利用施設19と第三設備4とをパイプラインで接続して、当該パイプラインを介して廃水蒸気を第三設備4のメタン発酵装置14に移送し、メタン発酵装置14に貯留された水熱処理液の加温に利用することができる。
The gas utilization facility 19 is a power plant that generates electricity with a steam turbine, and at least one of the first facility 2, the second facility 3, and the third facility 4 and the gas utilization facility 19 are installed close to each other. If so, use the waste steam, which is the high-temperature steam after being used for power generation by the steam turbine of the gas utilization facility 19, in the adjacent first facility 2, second facility 3, or third facility 4. Can be done.
For example, when the gas utilization facility 19 equipped with a steam turbine is installed close to the first facility 2, the gas utilization facility 19 and the first facility 2 are connected by a pipeline and via the pipeline. The waste steam can be transferred to the hydrothermal treatment apparatus 10 of the first equipment 2 and used as high-temperature and high-pressure steam used by the hydrothermal treatment apparatus 10 or as a part thereof.
When the gas utilization facility 19 equipped with the steam turbine is installed close to the second facility 3, the gas utilization facility 19 and the second facility 3 are connected by a pipeline and via the pipeline. The waste steam can be transferred to the solubilization tank 13 of the second facility 3 and used for heating the hydrothermal treatment liquid stored in the solubilization tank 13.
Further, when the gas utilization facility 19 equipped with the steam turbine is installed close to the third facility 4, the gas utilization facility 19 and the third facility 4 are connected by a pipeline and via the pipeline. The waste steam can be transferred to the methane fermentation apparatus 14 of the third facility 4 and used for heating the hydrothermal treatment liquid stored in the methane fermentation apparatus 14.

さらに、ガスエンジンを備えたガス利用施設19が、第二設備3に近接して設置されている場合、ガス利用施設19と第二設備3とをパイプラインで接続して、当該パイプラインを介して上記熱回収装置で生成された温水を第二設備3の可溶化槽13に移送し、可溶化槽13に貯留された水熱処理液の加温に利用することができる。
同様に、ガスエンジンを備えたガス利用施設19が、第三設備4に近接して設置されている場合、また、ガス利用施設19と第三設備4とをパイプラインで接続して、当該パイプラインを介して当該温水を第三設備4のメタン発酵装置14に移送し、メタン発酵装置14に貯留された水熱処理液の加温に利用することができる。
上述のように、可溶化槽13の加温の温度は約40℃〜60℃、また、メタン発酵装置14の加温の温度は約37℃もしくは約55℃であるので、可溶化槽13やメタン発酵装置14を加温するには、廃水蒸気よりも温水の方が取り扱いやすい。
Further, when the gas utilization facility 19 equipped with the gas engine is installed close to the second facility 3, the gas utilization facility 19 and the second facility 3 are connected by a pipeline and via the pipeline. The hot water generated by the heat recovery device can be transferred to the solubilization tank 13 of the second facility 3 and used for heating the hydrothermal treatment liquid stored in the solubilization tank 13.
Similarly, when the gas utilization facility 19 equipped with the gas engine is installed close to the third facility 4, the gas utilization facility 19 and the third facility 4 are connected by a pipeline to the pipe. The hot water can be transferred to the methane fermentation apparatus 14 of the third facility 4 via the line and used for heating the hydrothermal treatment liquid stored in the methane fermentation apparatus 14.
As described above, the heating temperature of the solubilization tank 13 is about 40 ° C. to 60 ° C., and the heating temperature of the methane fermentation apparatus 14 is about 37 ° C. or about 55 ° C. To heat the methane fermentation apparatus 14, warm water is easier to handle than waste steam.

このように、ガス利用施設19が蒸気タービンを備えている場合、蒸気タービンから排出される廃水蒸気を熱源として水熱処理システム1内で利用でき、また、ガス利用施設19がガスエンジンを備えている場合、上記熱回収装置で生成される温水を熱源として水熱処理システム1内で利用できるため、水熱処理システム1のコストパフォーマンスをさらに向上することができる。 As described above, when the gas utilization facility 19 is equipped with a steam turbine, the waste steam discharged from the steam turbine can be used as a heat source in the hydrothermal treatment system 1, and the gas utilization facility 19 is equipped with a gas engine. In this case, since the hot water generated by the heat recovery device can be used in the hydrothermal treatment system 1 as a heat source, the cost performance of the hydrothermal treatment system 1 can be further improved.

第四移送装置24は、第二設備3の加圧分離装置12で分離された残余物を、後述の廃棄物焼却施設20へ移送する装置である。
第二設備3と廃棄物焼却施設20とが互いに近接して設置されている場合、第四移送装置24は、加圧分離装置12の残余物の排出口と廃棄物焼却施設20のごみピットとに接続し、且つ、加圧分離装置12から排出された残余物をごみピットへ移送するコンベヤが望ましい。
一方、第二設備3と廃棄物焼却施設20とが互いに遠方に設置されている場合、第四移送装置24は、トラックやゴミ収集車などの自動車が望ましい。この場合は、加圧分離装置12から排出された残余物をトラックの荷台やごみ収集車内へ積載または貯留し、廃棄物焼却施設20へ移送することができる。
The fourth transfer device 24 is a device that transfers the residue separated by the pressure separation device 12 of the second facility 3 to the waste incinerator 20 described later.
When the second facility 3 and the waste incinerator 20 are installed close to each other, the fourth transfer device 24 is a waste discharge port of the pressure separation device 12 and a waste pit of the waste incinerator 20. It is desirable that the conveyor is connected to the waste pit and transfers the residue discharged from the pressure separating device 12 to the waste pit.
On the other hand, when the second facility 3 and the waste incinerator 20 are installed far from each other, the fourth transfer device 24 is preferably an automobile such as a truck or a garbage truck. In this case, the residue discharged from the pressure separation device 12 can be loaded or stored in the truck bed or the garbage collection vehicle and transferred to the waste incinerator 20.

廃棄物焼却施設20は、廃棄物を焼却炉で焼却する施設であり、第二設備3の加圧分離装置12から排出された残余物及び脱水機15で分離された脱水汚泥も焼却することができる。廃棄物焼却施設20は、焼却炉で生じた熱により、ボイラーで高温高圧の水蒸気を生成し、この高温高圧の水蒸気で蒸気タービンを回すことで、発電することができる。
第一設備2と第二設備3と第三設備4の少なくともいずれか一つと廃棄物焼却施設20とが互いに近接して設置されている場合、廃棄物焼却施設20の蒸気タービンで発電に利用された後の高温の水蒸気である廃水蒸気を当該近接している第一設備2や第二設備3や第三設備4で利用することができる。
例えば、廃棄物焼却施設20が、第一設備2と近接して設置されている場合、廃棄物焼却施設20と第一設備2とをパイプラインで接続して、当該パイプラインを介して廃水蒸気を第一設備2の水熱処理装置10に移送し、水熱処理装置10が使用する高温高圧の水蒸気として又はその一部として利用することができる。
また、廃棄物焼却施設20が、第二設備3に近接して設置されている場合、廃棄物焼却施設20と第二設備3とをパイプラインで接続して、当該パイプラインを介して廃水蒸気を第二設備3の可溶化槽13に移送し、可溶化槽13に貯留された水熱処理液の加温に利用することができる。
さらに、廃棄物焼却施設20が、第三設備4に近接して設置されている場合、廃棄物焼却施設20と第三設備4とをパイプラインで接続して、当該パイプラインを介して廃水蒸気を第三設備4のメタン発酵装置14に移送し、メタン発酵装置14に貯留された水熱処理液の加温に利用することができる。
このように、廃棄物焼却施設20の廃水蒸気を熱源として水熱処理システム1内で有効に利用できるため、水熱処理システム1のコストパフォーマンスをさらに向上することができる。
The waste incinerator 20 is a facility that incinerates waste in an incinerator, and can also incinerate the residue discharged from the pressure separating device 12 of the second facility 3 and the dehydrated sludge separated by the dehydrator 15. it can. The waste incinerator 20 can generate electricity by generating high-temperature and high-pressure steam in a boiler by the heat generated in the incinerator and turning a steam turbine with the high-temperature and high-pressure steam.
When at least one of the first facility 2, the second facility 3, and the third facility 4 and the waste incinerator 20 are installed close to each other, the steam turbine of the waste incinerator 20 is used for power generation. The waste steam, which is the high-temperature steam after that, can be used in the adjacent first equipment 2, second equipment 3, and third equipment 4.
For example, when the waste incinerator 20 is installed close to the first facility 2, the waste incinerator 20 and the first facility 2 are connected by a pipeline, and the waste steam is connected through the pipeline. Can be transferred to the hydrothermal treatment apparatus 10 of the first equipment 2 and used as high-temperature and high-pressure steam used by the hydrothermal treatment apparatus 10 or as a part thereof.
When the waste incinerator 20 is installed close to the second facility 3, the waste incinerator 20 and the second facility 3 are connected by a pipeline, and waste steam is discharged through the pipeline. Can be transferred to the solubilization tank 13 of the second facility 3 and used for heating the hydrothermal treatment liquid stored in the solubilization tank 13.
Further, when the waste incinerator 20 is installed close to the third facility 4, the waste incinerator 20 and the third facility 4 are connected by a pipeline, and the waste steam is connected through the pipeline. Can be transferred to the methane incinerator 14 of the third facility 4 and used for heating the hydrothermal treatment liquid stored in the methane incinerator 14.
As described above, since the waste steam of the waste incinerator 20 can be effectively used in the hydrothermal treatment system 1 as a heat source, the cost performance of the hydrothermal treatment system 1 can be further improved.

なお、水熱処理システム1は、(1)解繊液供給装置17、(2)し尿受入槽18、(3)第三移送装置23及びガス利用施設19、(4)第四移送装置24及び廃棄物焼却施設20の四つのうち、いずれも具備しないシステムであってもよいし、いずれか一つ、二つまたは三つのみ具備するシステムであってもよいし、四つ全てを具備するシステムであってもよい。 The hydrothermal treatment system 1 includes (1) a defibrating liquid supply device 17, (2) a urine receiving tank 18, (3) a third transfer device 23 and a gas utilization facility 19, (4) a fourth transfer device 24, and disposal. A system that does not have any of the four incinerators 20, a system that has only one, two, or three, or a system that has all four. There may be.

1 水熱処理システム
2 第一設備
3 第二設備
4 第三設備
10 水熱処理装置
11 調整槽
12 加圧分離装置
12A 回転式ドラムスクリーン
12B スクリュープレス
13 可溶化槽
14 メタン発酵装置
15 脱水機
16 廃液処理装置(し尿処理施設)
17 解繊液供給装置
18 し尿受入槽
19 ガス利用施設
20 廃棄物焼却施設
21 第一移送装置
22 第二移送装置
23 第三移送装置
24 第四移送装置
25 供給路
1 Hydrothermal treatment system 2 1st equipment 3 2nd equipment 4 3rd equipment 10 Hydrothermal treatment equipment 11 Adjustment tank 12 Pressurized separation equipment 12A Rotary drum screen 12B Screw press 13 Solubilization tank 14 Methan fermentation equipment 15 Dehydrator 16 Waste liquid treatment Equipment (sewage treatment facility)
17 Defibering liquid supply device 18 Human waste receiving tank 19 Gas utilization facility 20 Waste incinerator 21 1st transfer device 22 2nd transfer device 23 3rd transfer device 24 4th transfer device 25 Supply channel

Claims (5)

有機物含有廃棄物を水熱反応させる水熱処理装置と、
前記水熱反応された水熱処理物を加湿する調整槽と、
前記調整槽で加湿された水熱処理物を移送する第一移送装置と、
前記第一移送装置で移送された水熱処理物を加圧して水熱処理液と残余物とに分離する加圧分離装置と、
前記加圧分離装置で分離された水熱処理液を貯留して加温する可溶化槽と、
前記可溶化槽で加温され且つ可溶化された水熱処理液を前記調整槽に返送する第二移送装置と、
前記可溶化槽に貯留された水熱処理液を用いてメタンガスと消化液を生成するメタン発酵装置と
前記消化液を脱水汚泥と脱水分離液に分離する脱水機と、
前記脱水分離液を少なくとも硝化及び脱窒素して再利用水を生成する廃液処理装置と
を有し、
前記第二移送装置は、前記可溶化槽に貯留された水熱処理液に含まれる有機物の濃度が微生物または菌によるメタンガスの生成に適した有機物の濃度である所定濃度未満の場合に、前記調整槽に前記水熱処理液を返送し、前記有機物の濃度が前記所定濃度以上の場合に、前記メタン発酵装置に前記水熱処理液を移送する水熱処理システム。
A hydrothermal treatment device that reacts organic matter-containing waste with water heat,
An adjustment tank that humidifies the hydrothermally reacted hydrothermally treated product, and
The first transfer device that transfers the hydrothermally treated product humidified in the adjustment tank, and
A pressure separation device that pressurizes the hydrothermally treated product transferred by the first transfer device and separates it into a hydrothermal treatment liquid and a residue.
A solubilization tank that stores and heats the hydrothermal treatment solution separated by the pressure separation device, and
A second transfer device that returns the hydrothermal treatment solution that has been heated and solubilized in the solubilization tank to the adjustment tank.
A methane fermentation apparatus that produces methane gas and digestive juice using the hydrothermal treatment liquid stored in the solubilization tank, a dehydrator that separates the digestive juice into dehydrated sludge and dehydrated separate liquid,
It has a waste liquid treatment device that at least nitrifies and denitrifies the dehydrated separation liquid to generate recycled water.
The second transfer device, when less than the predetermined concentration levels of organic matter contained in the hydrothermal treatment liquid stored in the solubilization tank is at a concentration of organic substances which are suitable for the generation of methane by microorganisms or fungi, said adjusting tank A hydrothermal treatment system that returns the hydrothermal solution to the methane fermentation apparatus and transfers the hydrothermal solution to the methane fermentation apparatus when the concentration of the organic substance is equal to or higher than the predetermined concentration.
紙類を解繊した解繊液を前記消化液に供給する解繊液供給装置をさらに有する請求項1に記載の水熱処理システム。 The hydrothermal treatment system according to claim 1, further comprising a defibration liquid supply device that supplies a defibration liquid obtained by defibrating paper to the digestive liquid. し尿を貯留するし尿受入槽をさらに有し、
前記し尿受入槽のし尿を前記メタン発酵装置に供給して前記水熱処理液と混合し、
または、前記し尿受入槽のし尿を前記消化液に混合し、
または、前記し尿受入槽のし尿を前記脱水分離液に混合する請求項1または請求項2のいずれか一項に記載の水熱処理システム。
It also has a human waste receiving tank to store human waste,
The human waste from the human waste receiving tank is supplied to the methane fermentation apparatus and mixed with the hydrothermal treatment liquid.
Alternatively, the human waste from the human waste receiving tank is mixed with the digestive juice to mix it with the digestive juice.
Alternatively, the hydrothermal treatment system according to claim 1 or 2, wherein the human waste from the human waste receiving tank is mixed with the dehydration separation liquid.
前記加圧分離装置は、
前段に回転式ドラムスクリーン及び後段にスクリュープレスを備え、
前記回転式ドラムスクリーンで分離される水熱処理液と、前記スクリュープレスで分離される水熱処理液とが、前記可溶化槽に貯留される請求項3に記載の水熱処理システム。
The pressure separation device is
Equipped with a rotary drum screen in the front stage and a screw press in the rear stage
The hydrothermal treatment system according to claim 3, wherein the hydrothermal treatment liquid separated by the rotary drum screen and the hydrothermal treatment liquid separated by the screw press are stored in the solubilization tank.
前記メタン発酵装置で生成されたメタンガスを移送する第三移送装置及び前記第三移送装置で移送されたメタンガスを利用するガス利用施設と、
または、
前記加圧分離装置で分離された残余物を移送する第四移送装置及び前記第四移送装置で移送された残余物を焼却する廃棄物焼却施設と
をさらに有し、
前記水熱処理装置及び前記調整槽と、前記加圧分離装置及び前記可溶化槽とが、近接して設置されている場合、前記第一移送装置は破砕ポンプを備えたパイプラインであり、前記第二移送装置はポンプを備えたパイプラインであり、
前記水熱処理装置及び前記調整槽と、前記加圧分離装置及び前記可溶化槽とが、互いに遠方に設置されている場合、前記第一移送装置及び前記第二移送装置は、いずれも自動車であり、
前記メタン発酵装置と前記ガス利用施設とが近接して設置されている場合、前記第三移送装置はパイプラインであり、
前記メタン発酵装置と前記ガス利用施設とが、互いに遠方に設置されている場合、前記第三移送装置は自動車であり、
前記廃棄物焼却施設と、前記加圧分離装置及び前記可溶化槽とが、近接して設置されている場合、前記第四移送装置はコンベヤであり、
前記廃棄物焼却施設と、前記加圧分離装置及び前記可溶化槽とが、互いに遠方に設置されている場合、前記第四移送装置は自動車であり、
前記ガス利用施設は蒸気タービンまたはガスエンジンを備え、前記蒸気タービンで発電に利用された水蒸気を、前記水熱処理装置及び前記可溶化槽及び前記メタン発酵装置の少なくともいずれか一つに供給し、または、前記ガスエンジンで生じた排ガスから生成した温水を、前記可溶化槽及び前記メタン発酵装置の少なくとも一方に供給し、
前記廃棄物焼却施設は蒸気タービンを備え、前記蒸気タービンで発電に利用された水蒸気を、前記水熱処理装置及び前記可溶化槽及び前記メタン発酵装置の少なくともいずれか一つに供給し、
前記廃液処理装置はし尿処理施設であって前記再利用水は前記調整槽に供給される請求項4に記載の水熱処理システム。
A third transfer device that transfers the methane gas produced by the methane fermentation apparatus, a gas utilization facility that uses the methane gas transferred by the third transfer apparatus, and a gas utilization facility.
Or
It also has a fourth transfer device that transfers the residue separated by the pressure separation device and a waste incinerator that incinerates the residue transferred by the fourth transfer device.
When the hydrothermal treatment device and the adjustment tank and the pressure separation device and the solubilization tank are installed close to each other, the first transfer device is a pipeline provided with a crushing pump, and the first transfer device is a pipeline. (Ii) The transfer device is a pipeline equipped with a pump,
When the hydrothermal treatment device and the adjustment tank and the pressure separation device and the solubilization tank are installed far from each other, the first transfer device and the second transfer device are both automobiles. ,
When the methane fermentation apparatus and the gas utilization facility are installed in close proximity to each other, the third transfer apparatus is a pipeline.
When the methane fermentation device and the gas utilization facility are installed far from each other, the third transfer device is an automobile.
When the waste incinerator, the pressure separation device, and the solubilization tank are installed close to each other, the fourth transfer device is a conveyor.
When the waste incinerator, the pressure separation device, and the solubilization tank are installed far from each other, the fourth transfer device is an automobile.
The gas utilization facility is equipped with a steam turbine or a gas engine, and supplies steam used for power generation by the steam turbine to at least one of the hydrothermal treatment apparatus, the solubilization tank, and the methane fermentation apparatus, or , Hot water generated from the exhaust gas generated by the gas engine is supplied to at least one of the solubilization tank and the methane fermentation apparatus.
The waste incinerator is equipped with a steam turbine, and the steam used for power generation by the steam turbine is supplied to at least one of the hydrothermal treatment apparatus, the solubilization tank, and the methane fermentation apparatus.
The water heat treatment system according to claim 4, wherein the waste liquid treatment device is a urine treatment facility, and the reused water is supplied to the adjustment tank.
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