JP2879199B2 - Organic waste mineralization system - Google Patents

Organic waste mineralization system

Info

Publication number
JP2879199B2
JP2879199B2 JP7055199A JP5519995A JP2879199B2 JP 2879199 B2 JP2879199 B2 JP 2879199B2 JP 7055199 A JP7055199 A JP 7055199A JP 5519995 A JP5519995 A JP 5519995A JP 2879199 B2 JP2879199 B2 JP 2879199B2
Authority
JP
Japan
Prior art keywords
waste
catalyst
wet oxidation
organic
organic waste
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP7055199A
Other languages
Japanese (ja)
Other versions
JPH08224565A (en
Inventor
美津夫 小口
孔治 大坪
正治 渡邉
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
KAGAKU GIJUTSUCHO KOKU UCHU GIJUTSU KENKYUSHOCHO
TAIATSU GARASU KOGYO KK
Original Assignee
KAGAKU GIJUTSUCHO KOKU UCHU GIJUTSU KENKYUSHOCHO
TAIATSU GARASU KOGYO KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by KAGAKU GIJUTSUCHO KOKU UCHU GIJUTSU KENKYUSHOCHO, TAIATSU GARASU KOGYO KK filed Critical KAGAKU GIJUTSUCHO KOKU UCHU GIJUTSU KENKYUSHOCHO
Priority to JP7055199A priority Critical patent/JP2879199B2/en
Publication of JPH08224565A publication Critical patent/JPH08224565A/en
Application granted granted Critical
Publication of JP2879199B2 publication Critical patent/JP2879199B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、固形物を含む有機廃棄
物の無公害処理及び再利用を可能とする処理システムに
関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a treatment system that enables non-polluting treatment and reuse of organic waste containing solid matter.

【0002】[0002]

【従来の技術】従来、固形物を含む有機廃棄物の処理
は、それに含まれる排水の処理を主たる対象としてお
り、処理液は河川あるいは海に放流し、排ガスは大気中
に放出している。また固形状の有機廃棄物は、微生物に
よる分解、焼却、埋め立て等によっている。しかし、微
生物分解では活性汚泥の発生、焼却ではばい煙や有害物
質の発生、埋め立てでは処理場の不足、悪臭や水質汚染
の発生等、環境汚染の問題が深刻化している。
2. Description of the Related Art Conventionally, the treatment of organic waste containing solids is mainly intended for the treatment of wastewater contained therein, and the treated liquid is discharged into rivers or the sea, and the exhaust gas is discharged into the atmosphere. Solid organic waste is obtained by decomposition, incineration, landfill, and the like by microorganisms. However, environmental pollution problems such as activated sludge are generated in the case of microbial decomposition, soot and harmful substances are generated in the case of incineration, treatment plants are short in landfills, and odors and water pollution are becoming more serious.

【0003】[0003]

【発明が解決しようとする課題】本発明は、固形状のも
のを含む有機廃棄物を、外界から独立したシステムによ
って分解し、生成物を再利用することにより、無公害処
理を可能にするシステムを得ようとするものである。
SUMMARY OF THE INVENTION The present invention provides a system for decomposing organic waste, including solid waste, by decomposing the waste by a system independent of the outside world and reusing the product to thereby achieve pollution-free treatment. It is trying to get.

【0004】[0004]

【課題を解決するための手段】上記目的を達成するた
め、本発明のシステムは、廃棄物に含まれる固形状有機
物をスラリー状にする手段と、該スラリーに含まれる有
機物を湿式酸化容器中で高温高圧で酸化分解・液化する
手段と、該液化した処理液を触媒により無機化する手段
とからなり、さらに前記各手段から発生する処理液及び
排ガスを利用した植物栽培手段を含む。上記湿式酸化容
器は、空気添加装置と撹拌手段とを含んでもよく、触媒
による無機化手段は、高温高圧循環ポンプを用いて処理
液を触媒に循環接触させて分解を促進する。また、湿式
酸化処理過程で発生する排熱の回収、再利用システムを
含む。
In order to achieve the above object, a system according to the present invention comprises a means for converting solid organic substances contained in waste into a slurry, and a method for converting organic substances contained in the slurry into a wet oxidation vessel. It comprises means for oxidative decomposition and liquefaction at high temperature and pressure, and means for mineralizing the liquefied treatment liquid with a catalyst, and further includes a plant cultivation means utilizing the treatment liquid and exhaust gas generated from each of the above means. The wet oxidation container may include an air addition device and a stirring means, and the catalyst mineralization means promotes decomposition by circulating the treatment liquid to the catalyst using a high-temperature and high-pressure circulation pump. It also includes a system for collecting and reusing waste heat generated during the wet oxidation process.

【0005】[0005]

【実施例】以下、本発明の廃棄物処理システムを、図面
を参照して実施例によって詳細に説明する。有機廃棄物
としては、生ゴミ、し尿、紙、木材、有機性産業廃棄物
等、固形物及び液体状のものを広く対象とすることがで
きる。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, a waste disposal system according to the present invention will be described in detail with reference to the drawings. As organic waste, solid and liquid forms such as garbage, human waste, paper, wood, organic industrial waste, and the like can be widely used.

【0006】図1は本発明の処理システムの一実施例の
フローシートである。有機廃棄物は、粉砕器を有する前
処理容器1で固形物が粉砕される。固形物が多い場合で
も、後述のように植物栽培施設からの廃液が加えられ
て、スラリー状にされる。生成したスラリーは、熱交換
器8を介して余熱され、移送ポンプ2によってバルブ9
を経て湿式酸化容器3に導入される。湿式酸化容器3で
は、スラリーは、酸化効率を高めるためにコンプレッサ
4により所定量の空気が添加された後、高温(250〜
300℃)に加熱され、含まれた有機物が酸化分解・液
化される。加熱の際、有機物に含まれる水分の気化を防
ぐために、湿式酸化容器3は密閉式高圧容器となってい
る。また、有機物の濃度が高い場合には、有機物と空気
が充分混ざるように、撹拌器5の使用も可能となってい
る。
FIG. 1 is a flow sheet of one embodiment of the processing system of the present invention. As for the organic waste, solids are crushed in a pretreatment container 1 having a crusher. Even when there is a large amount of solid matter, a waste liquid from a plant cultivation facility is added to form a slurry as described below. The generated slurry is preheated through the heat exchanger 8 and is transferred by the transfer pump 2 to the valve 9.
And then introduced into the wet oxidation container 3. In the wet oxidation container 3, after a predetermined amount of air is added by the compressor 4 to increase the oxidation efficiency, the slurry is heated to a high temperature (250 to
(300 ° C.), and the contained organic matter is oxidatively decomposed and liquefied. At the time of heating, the wet oxidation container 3 is a closed high-pressure container in order to prevent vaporization of water contained in the organic matter. When the concentration of the organic matter is high, the stirrer 5 can be used so that the organic matter and the air are sufficiently mixed.

【0007】湿式酸化容器3で液化された処理液は、バ
ルブ10を開けることによって、湿式酸化容器3内の圧
力で、予め湿式酸化容器3と同一条件に加熱された触媒
反応器6に導入される。触媒反応容器6では、高圧高温
循環ポンプ7を使用して、有機物を触媒と連続的に反復
反応させることにより、無機質と無機ガス(二酸化炭素
及び窒素ガス)に分解する。実施例では、触媒反応器6
からの未分解物をパイプで湿式酸化容器3へと循環させ
ているが、触媒反応器6だけで処理液を循環することも
可能である。
The processing liquid liquefied in the wet oxidation vessel 3 is introduced into the catalytic reactor 6 which has been heated to the same conditions as the wet oxidation vessel 3 in advance by opening the valve 10 at the pressure in the wet oxidation vessel 3. You. In the catalyst reaction vessel 6, an organic substance is continuously and repeatedly reacted with a catalyst by using a high-pressure and high-temperature circulation pump 7 to decompose into an inorganic substance and an inorganic gas (carbon dioxide and nitrogen gas). In the embodiment, the catalytic reactor 6
Although the undecomposed matter from is circulated to the wet oxidation vessel 3 by a pipe, the treatment liquid can be circulated only by the catalytic reactor 6.

【0008】この循環式の利点は、気相に含まれる酸素
を酸化分解時に効率よく処理液に混入させられることで
ある。また、湿式酸化容器3と触媒反応器6を独立させ
ているのは、従来方式では湿式酸化容器の中に触媒を封
入しているため、高濃度の有機物を処理すると、触媒に
有機物が付着してしまい、触媒の機能が劣化するので、
これを防ぐためである。
[0008] The advantage of this circulation system is that oxygen contained in the gas phase can be efficiently mixed into the processing solution during oxidative decomposition. Also, the reason why the wet oxidation vessel 3 and the catalyst reactor 6 are made independent is that the catalyst is sealed in the wet oxidation vessel in the conventional method, so that when high-concentration organic substances are treated, the organic substances adhere to the catalyst. And the function of the catalyst deteriorates.
This is to prevent this.

【0009】無機化された処理液には、植物の生育に必
要な成分が含まれているので、バルブ11を介して、植
物栽培施設13へ導入される。さらに、無機ガス(二酸
化炭素及び窒素ガス)も植物の生育に利用するために、
バルブ12を介して、植物栽培施設13へ導入される。
Since the mineralized treatment liquid contains components necessary for growing the plant, it is introduced into the plant cultivation facility 13 through the valve 11. In addition, in order to use inorganic gas (carbon dioxide and nitrogen gas) for plant growth,
It is introduced into the plant cultivation facility 13 via the valve 12.

【0010】湿式酸化容器3、触媒反応器6や配管系で
発生する熱はすべて回収され、熱交換器8及び植物栽培
施設13で利用する。また、植物栽培施設13から発生
した排液やゴミは前処理容器1に導入し、酸化分解後、
再利用する。
The heat generated in the wet oxidation container 3, the catalytic reactor 6, and the piping system is all recovered and used in the heat exchanger 8 and the plant cultivation facility 13. In addition, drainage and garbage generated from the plant cultivation facility 13 are introduced into the pretreatment container 1, and after oxidative decomposition,
Reuse.

【0011】図2は本発明の特徴の1つである連続処理
を実現する際に必要な高圧高温循環ポンプ7を示し、ポ
ンプ本体は下フタ21と上フタ22に分割できるように
なっている。液体を移送するための羽根23の回転は、
片側に永久磁石の内磁29が付いたシャフト24の回転
駆動により、また、シャフト24の回転は電磁式の密閉
型撹拌機30をベルトで外部から駆動することによって
発生する。そして羽根23の回転によって、下フタ21
のパイプから液体が羽根23の中心部に吸い上げられた
後、羽根23の回転力によって上フタ22のパイプから
外へ排出される。シャフト24の芯を出すために、スナ
ップリング25で押えられたベアリング26を用いてい
る。高圧高温環境に耐えるために、下フタ21と上フタ
22はパッキン27を用いてシール性を高め、六角ナッ
ト28で締め付けられる。
FIG. 2 shows a high-pressure and high-temperature circulating pump 7 necessary for realizing continuous processing which is one of the features of the present invention. The pump body can be divided into a lower lid 21 and an upper lid 22. . The rotation of the blade 23 for transferring the liquid
The rotation of the shaft 24 having the internal magnet 29 of the permanent magnet on one side is generated, and the rotation of the shaft 24 is generated by externally driving the electromagnetic closed stirrer 30 with a belt. The rotation of the blades 23 causes the lower lid 21 to rotate.
After the liquid is sucked up from the pipe at the center of the blade 23, the liquid is discharged from the pipe of the upper lid 22 by the rotational force of the blade 23. In order to center the shaft 24, a bearing 26 held by a snap ring 25 is used. In order to withstand a high-pressure and high-temperature environment, the lower lid 21 and the upper lid 22 are improved in sealing performance by using a packing 27 and are tightened by a hexagon nut 28.

【0012】処理例 本発明の具体的実施結果の一例を、表1にしたがって説
明する。有機廃棄物の原料として兎の糞を用い、その有
機物の濃度はCOD(Cr)で20,000ppm、ケ
ルダール性窒素は30,000ppmであった。真空引
きした内容積1リッターの湿式酸化容器3にこの有機廃
棄物(0.5リッター)を入れた後、酸化に必要な酸素
を2.5Mpa添加した。分解温度を320℃に設定
し、30分間加熱した。表1の一次処理は、従来方式の
触媒を使わない湿式酸化分解液の分析結果で、CODは
約80%、ケルダール性窒素は約98.8%程度酸化分
解されているが、アンモニアや酢酸が多く生成してい
る。
Processing Example An example of a specific implementation result of the present invention will be described with reference to Table 1. Rabbit feces were used as a raw material of the organic waste, and the concentration of the organic matter was 20,000 ppm in COD (Cr) and 30,000 ppm in Kjeldahl nitrogen. This organic waste (0.5 liter) was placed in a vacuum-evacuated wet oxidation container 3 having an internal volume of 1 liter, and oxygen required for oxidation was added at 2.5 Mpa. The decomposition temperature was set at 320 ° C. and heating was performed for 30 minutes. The primary treatment in Table 1 shows the results of analysis of a conventional wet oxidation decomposition solution that does not use a catalyst. COD is about 80% and Kjeldahl nitrogen is about 98.8%, but ammonia and acetic acid are not. Many have been generated.

【表1】 [Table 1]

【0013】そこで、一次処理液を同一環境で30分
間、触媒反応器6で触媒と連続的に反応させた。使用す
る触媒の1例を挙げれば、粒状あるいはペレット状のチ
タニア及びアルミナに、ルテニウム、パラジウムなどの
貴金属を担持したものを用いる。しかし、これに限られ
るわけではなく、例えば白金、ゼオライトのような触媒
も用いることができる。その結果、CODは約99.7
%、ケルダール性窒素は約99.97%分解された。し
かもアンモニア成分はごくわずかに存在するだけで、窒
素分のほとんどは植物の生育に必要な硝酸性窒素に変わ
っていた。さらに、酢酸は分析器の検出限界以下となっ
ていた。また、ガス成分を調べると、触媒を使わない一
次処理では、二酸化炭素濃度は約30%程度であるが、
触媒を使うと約50%まで増えている。これらの結果か
ら、本発明のシステムが有機廃棄物をいかに効率よく無
機物に変換できるかということがわかる。
Therefore, the primary treatment liquid was continuously reacted with the catalyst in the catalyst reactor 6 for 30 minutes in the same environment. As an example of the catalyst to be used, a catalyst in which noble metals such as ruthenium and palladium are supported on titania and alumina in the form of granules or pellets is used. However, the present invention is not limited to this. For example, a catalyst such as platinum or zeolite can be used. As a result, the COD is about 99.7
%, Kjeldahl nitrogen was decomposed by about 99.97%. In addition, only a small amount of the ammonia component was present, and most of the nitrogen content had been changed to nitrate nitrogen, which is necessary for plant growth. Furthermore, acetic acid was below the detection limit of the analyzer. In addition, when examining the gas components, in the primary treatment without using a catalyst, the carbon dioxide concentration is about 30%,
With the use of a catalyst, it has increased to about 50%. These results show how efficiently the system of the present invention can convert organic waste to inorganic.

【0014】本発明の実施例において、廃液、ガスの利
用施設として植物栽培施設を用いているが、具体的に
は、野菜や果樹などのいわゆる植物工場的なものから、
排熱も利用することによって熱帯植物園、水族館などに
も適応できる。また、必要に応じて、完全なクローズド
サイクルとせず、養液及びガスは、温室あるいは露地栽
培の栽培施設に供給することもできる。
In the embodiment of the present invention, a plant cultivation facility is used as a waste liquid and gas utilization facility. Specifically, a plant plant such as a vegetable or a fruit tree is used.
It can also be used in tropical botanical gardens and aquariums by utilizing waste heat. Further, if necessary, the nutrient solution and gas can be supplied to a greenhouse or a cultivation facility for open-field cultivation without using a complete closed cycle.

【0015】[0015]

【発明の効果】本発明は上述のように、固形物を含む有
機廃棄物を、外界から独立したシステム中で処理するの
で、環境汚染が生じない無公害処理であり、その廃液に
は植物の生育に必要な成分が含まれるので植物の養液と
なり、発生するガス、排熱も有効利用するなどして有機
廃棄物の再利用化を省エネルギー、省スペースで実現す
ることができる。
As described above, the present invention treats organic waste containing solid matter in a system independent of the outside world, so it is a pollution-free treatment that does not cause environmental pollution. Since it contains components necessary for growth, it becomes a nutrient solution for plants, and the generated gas and waste heat can be effectively used, so that organic waste can be reused with less energy and space.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明のシステムの1実施例を示すフローシー
トである。
FIG. 1 is a flow sheet showing one embodiment of the system of the present invention.

【図2】本発明のシステムに用いる高温高圧循環ポンプ
を示す組立図である。
FIG. 2 is an assembly view showing a high-temperature and high-pressure circulation pump used in the system of the present invention.

【符号の説明】[Explanation of symbols]

1 前処理容器 2 移送ポンプ 3 湿
式酸化容器 4 コンプレッサ 5 撹拌器 6 触
媒反応器 7 高圧高温循環ポンプ 8 熱
交換器 9,10,11,12 バルブ 13 植
物栽培施設 21 下フタ 22 上フタ 23
回転羽根 24 シャフト 25 スナップリング 26
ベアリング 27 パッキン 28 六角ナット 29
永久磁石 30 密閉型撹拌機
DESCRIPTION OF SYMBOLS 1 Pretreatment container 2 Transfer pump 3 Wet oxidation container 4 Compressor 5 Stirrer 6 Catalytic reactor 7 High pressure high temperature circulation pump 8 Heat exchanger 9, 10, 11, 12 Valve 13 Plant cultivation facility 21 Lower lid 22 Upper lid 23
Rotating blade 24 Shaft 25 Snap ring 26
Bearing 27 Packing 28 Hex nut 29
Permanent magnet 30 Closed stirrer

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平4−78496(JP,A) 特開 昭54−38271(JP,A) (58)調査した分野(Int.Cl.6,DB名) B09B 3/00 - 5/00 C02F 11/08 ──────────────────────────────────────────────────続 き Continuation of the front page (56) References JP-A-4-78496 (JP, A) JP-A-54-38271 (JP, A) (58) Fields investigated (Int. Cl. 6 , DB name) B09B 3/00-5/00 C02F 11/08

Claims (5)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 廃棄物に含まれる固形状有機物をスラリ
ー状にする手段と、該スラリーに含まれる有機物を湿式
酸化容器中で高温高圧で酸化分解・液化する手段と、該
液化した処理液を触媒により無機化する手段とからなる
ことを特徴とする有機廃棄物の無機化処理システム
1. A means for slurrying solid organic matter contained in waste, a means for oxidatively decomposing and liquefying organic matter contained in the slurry at a high temperature and a high pressure in a wet oxidation vessel, and A system for mineralizing organic waste, comprising means for mineralizing with a catalyst.
【請求項2】 上記湿式酸化容器が、空気添加装置と撹
拌手段とを含むことを特徴とする請求項1の有機廃棄物
の無機化処理システム
2. The organic waste mineralization system according to claim 1, wherein the wet oxidation container includes an air addition device and a stirring means.
【請求項3】 上記触媒による無機化手段は、高温高圧
循環ポンプを用いて処理液を触媒に循環接触させること
を特徴とする請求項1あるいは2のいずれかの有機廃棄
物の無機化処理システム
3. The organic waste mineralization system according to claim 1, wherein the catalyst mineralization means circulates the treatment liquid to the catalyst using a high-temperature and high-pressure circulation pump.
【請求項4】 上記湿式酸化処理過程で発生する排熱の
回収、再利用システムを含むことを特徴とする請求項1
ないし3のいずれかの有機廃棄物の無機化処理システム
4. The system according to claim 1, further comprising a system for recovering and recycling exhaust heat generated in the wet oxidation process.
Or inorganic waste treatment system for organic waste
【請求項5】 廃棄物に含まれる固形状有機物をスラリ
ー状にする手段と、該スラリーに含まれる有機物を湿式
酸化容器中で高温高圧で酸化分解・液化する手段と、該
液化した処理液を触媒により無機化する手段と、前記各
手段から発生する処理液及び排ガスを利用した植物栽培
手段からなることを特徴とする有機廃棄物の無機化処理
システム
5. A means for converting a solid organic substance contained in waste into a slurry, a means for oxidatively decomposing and liquefying an organic substance contained in the slurry at a high temperature and a high pressure in a wet oxidation vessel, and A system for mineralizing organic waste, comprising: means for mineralizing with a catalyst; and plant cultivation means using a treatment liquid and exhaust gas generated from each of the means.
JP7055199A 1995-02-21 1995-02-21 Organic waste mineralization system Expired - Fee Related JP2879199B2 (en)

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JP2879199B2 true JP2879199B2 (en) 1999-04-05

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JP2002066507A (en) * 2000-08-25 2002-03-05 Ishikawajima Harima Heavy Ind Co Ltd Treating method for organic solid and treating device for organic solid
JP2002102870A (en) * 2000-09-28 2002-04-09 Ishikawajima Harima Heavy Ind Co Ltd Method and device for treating organic resin waste such as coating material-containing waste liquid and coating material peeling liquid
JP4944425B2 (en) * 2004-12-16 2012-05-30 パナソニック株式会社 Garbage disposal equipment

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