JP2002200471A - Decomposition treatment equipment for organic waste - Google Patents

Decomposition treatment equipment for organic waste

Info

Publication number
JP2002200471A
JP2002200471A JP2000403099A JP2000403099A JP2002200471A JP 2002200471 A JP2002200471 A JP 2002200471A JP 2000403099 A JP2000403099 A JP 2000403099A JP 2000403099 A JP2000403099 A JP 2000403099A JP 2002200471 A JP2002200471 A JP 2002200471A
Authority
JP
Japan
Prior art keywords
decomposition
stirring
organic waste
granular
tank
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.)
Granted
Application number
JP2000403099A
Other languages
Japanese (ja)
Other versions
JP2002200471A5 (en
JP3624832B2 (en
Inventor
Takayoshi Yamamoto
隆祥 山本
Manabu Isozaki
學 五十崎
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.)
KAWASAKI UNYU KIKO KK
Original Assignee
KAWASAKI UNYU KIKO 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 KAWASAKI UNYU KIKO KK filed Critical KAWASAKI UNYU KIKO KK
Priority to JP2000403099A priority Critical patent/JP3624832B2/en
Publication of JP2002200471A publication Critical patent/JP2002200471A/en
Publication of JP2002200471A5 publication Critical patent/JP2002200471A5/ja
Application granted granted Critical
Publication of JP3624832B2 publication Critical patent/JP3624832B2/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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Abstract

PROBLEM TO BE SOLVED: To provide an organic waste treatment equipment capable of reducing the volume of organic waste such as biomass, by simple treatment operation. SOLUTION: This equipment for performing biological decomposition treatment, or biological decomposition treatment and drying treatment of organic waste, has: a horizontal drum type decomposition/agitation vessel placed inside the equipment; a charge port for organic waste or the like, which is opened in the upper part of the decomposition/agitation vessel on its front side; an agitation mechanism consisting of a rotary shaft placed so as to horizontally extend through the inside of the decomposition/agitation vessel, and plural agitation bars each vertically fitted to the rotary shaft; a granular agitation medium on which microorganisms are grown and with which the inside of the decomposition/agitation vessel is packed; and a discharge port which is used for withdrawing the granular agitation medium and a decomposition product inside the horizontal drum type decomposition/agitation vessel and placed at such a position on the rear side of the decomposition/agitation vessel, as to be opposite to the charge port.

Description

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

【0001】[0001]

【発明の属する分野】本発明は有機性廃棄物又はその含
有廃棄物を乾燥し又は微生物、熱、或いは空気等の作用
により分解して乾燥減量し堆肥、肥効性物質、飼料、無
害化土壌、抽出して有用物を回収する原料、その他の有
用固形物として回収し、又は減量無害化、乾燥処理する
装置に関する。
The present invention relates to organic wastes or wastes containing the same, which are dried or decomposed by the action of microorganisms, heat, air, etc. to reduce the weight of the wastes, thereby reducing compost, fertilizer, feed, detoxified soil. The present invention relates to an apparatus for extracting and recovering useful substances by extracting the raw materials and other useful solid substances, or for performing detoxification and drying treatment.

【0002】[0002]

【従来の技術及び発明が解決しようとする課題】従来、
有機性廃棄物、農林・水産副産物、有害物で汚染された
有機性土状物質或いは土壌を簡易に微細化処理しあるい
は有用化する装置は少なかった。還元性雰囲気で処理し
て無害化する簡易な装置もなかった。回転炉、回転粉砕
機のように連続的押し出し流れの比較的大型装置はあっ
たがドラムを回転しない小型のこの種の装置は難かしか
った。有機性廃棄物を堆肥化又は減量する装置として
は、撹拌装置上部に有機性廃棄物の投入口を有し内部に
有機性廃棄物とともに微生物を着生した木材チップ、お
が屑等の粒状体、木片を投入・充填して撹拌するものが
あった。またこの撹拌槽に有機性廃棄物と硬質かつ多孔
質球状の粒状撹拌媒体を共存させ混合撹拌する撹拌機構
及びその内部を加熱する加熱手段及びその内部に外気を
通気する空気調和手段を設けたものがあった。そして、
前記装置には有機性廃棄物を粉砕し、発酵処理及び乾燥
処理をして堆肥化物を生成し、粒状撹拌媒体粒状体を分
離する機構を有しているものもあった。
2. Description of the Related Art
There have been few devices for easily pulverizing or using organic soil materials or soil contaminated with organic waste, agriculture, forestry and fishery by-products, and harmful substances. There was no simple device for detoxifying by treating in a reducing atmosphere. Although there were relatively large devices for continuous extrusion flow such as rotary furnaces and rotary crushers, small devices of this type which did not rotate the drum were difficult. As a device for composting or reducing the amount of organic waste, there are an input port for organic waste at the top of the stirrer, wood chips on which microorganisms have formed along with the organic waste, granular materials such as sawdust, and wood chips. Was charged and filled and stirred. In addition, a stirring mechanism for mixing and stirring the organic waste and the hard and porous spherical granular stirring medium in this stirring tank, a heating means for heating the inside thereof, and an air conditioning means for ventilating outside air are provided therein. was there. And
Some of the above-mentioned apparatuses have a mechanism for pulverizing organic waste, performing fermentation treatment and drying treatment to produce compost, and separating granular agitation medium particles.

【0003】しかしながら、有機性廃棄物、生ゴミ等の
堆肥化工程としての撹拌・粉砕工程、乾燥又は発酵工程
及び乾燥工程が分解・撹拌槽内の同一箇所で進められる
ため、堆肥化工程の最中に、追加の有機性廃棄物を投入
すると互いに混合し、先に投入した分が堆肥化終了して
も追加分の堆肥化が完了するまで取り出せない問題があ
った。消滅型操作の場合でも分解物だけを取り出すこと
が難かしかった。槽底に多孔板を設けて混合物を細粒化
した堆肥化物又は分解物を分離する方法もあったが、こ
の方法では撹拌粉砕工程で細粒化したが発酵・乾燥工程
が終了していない有機性廃棄物も孔を通過して分解物中
に未熟堆肥又は未分解物として排出される難点があっ
た。しかも従来装置では有機性廃棄物又は必要程度に乾
燥していない粘性の有機廃棄物がその上方の堆積物圧と
撹拌圧によって変形して孔と多孔板表面に付着して孔が
詰まり清掃作業を頻繁に行わなければならなかった。
[0003] However, since the stirring / crushing step, the drying or fermentation step, and the drying step as the composting step for composting organic waste and garbage are performed in the same place in the decomposition / stirring tank, the composting step is the most important. There is a problem in that when additional organic waste is added, it is mixed with each other and cannot be taken out until the additional composting is completed even if the first input is completed. Even in the case of an annihilation type operation, it was difficult to take out only the decomposition product. There was also a method of separating compost or decomposed product obtained by pulverizing the mixture by providing a perforated plate at the bottom of the tank. There is also a problem that the municipal waste also passes through the pores and is discharged into the decomposed product as immature compost or undegraded product. Moreover, in the conventional apparatus, the organic waste or the viscous organic waste that has not been dried to the extent necessary is deformed by the deposit pressure and the stirring pressure above it and adheres to the holes and the surface of the perforated plate, and the holes are clogged and cleaning work is performed. Had to be done frequently.

【0004】また微生物の活動を高めるための分解・撹
拌槽壁の加温又は保温において、外置の設備による温水
を分解・撹拌槽に循環する方法があったが、配管等から
の熱損失が大きく槽の各位置の壁面温度を制御温度に維
持することが難しく風雨等の外乱への対応も難かしく熱
効率もよいものではなく、臭気問題もあった。
[0004] In addition, there has been a method of circulating hot water by means of external equipment to the decomposition / stirring tank for heating or keeping the temperature of the decomposition / stirring tank to enhance the activity of microorganisms. It is difficult to maintain the wall temperature at each position of the tank at the control temperature, it is difficult to cope with disturbances such as wind and rain, the heat efficiency is not good, and there is an odor problem.

【0005】[0005]

【課題を解決するための手段】本発明は上記従来技術の
課題を解決するものであり、下記構成の有機性廃棄物等
の分解処理装置である。 (1)装置内部の横置ドラム型の分解・撹拌槽の前方上
部に開口された有機性廃棄物等の投入口を有し、その分
解・撹拌槽内には横貫して設置された回転シャフトと、
その回転シャフトに垂設された複数の撹拌棒からなる撹
拌機構を有し、また分解・撹拌槽の壁面には排出口を有
し、さらに分解・撹拌槽内には微生物が着生した粒状撹
拌媒体が充填され、かつ装置側面又は後部には開口され
た排気口、その排気口より脱臭装置を介して排気ブロア
ーにつながる雰囲気調節機構を備えた有機性廃棄物を微
生物分解処理又は微生物分解処理及び乾燥処理する有機
性廃棄物の分解処理装置において、前記横置ドラム型の
分解・撹拌槽内の前記粒状撹拌媒体及び分解物を取り出
す排出口が前記投入口に対置した後方の位置に設置して
なることを特徴とする有機性廃棄物の分解処理装置。 (2)分離・撹拌槽の側部に斜設された少なくとも底部
の一部に多数のスリット又は篩い目を有する分離用スロ
ープ、及び同分離用スロープに振動を与える振動機構よ
りなる分解物・粒状撹拌媒体分離装置を備えたことを特
徴とする前項1に記載の有機性廃棄物の分解処理装置。
SUMMARY OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, and is an apparatus for decomposing organic waste or the like having the following structure. (1) An input port for organic waste, etc., which is opened at the upper front of a horizontal drum type disassembly / stirring tank inside the apparatus, and a rotating shaft installed through the disassembly / stirring tank in a transverse direction When,
It has a stirring mechanism consisting of a plurality of stirring rods suspended from the rotating shaft, has a discharge port on the wall of the decomposition / stirring tank, and has granular stirring with microorganisms in the decomposition / stirring tank. A medium is filled, and an exhaust port opened on the side or rear of the apparatus, and an organic waste provided with an atmosphere control mechanism connected to an exhaust blower through a deodorizing device from the exhaust port by microbial decomposition treatment or microbial decomposition treatment. In the organic waste decomposition treatment apparatus to be dried, the discharge port for taking out the granular stirring medium and the decomposition product in the horizontal drum-type decomposition / stirring tank is installed at a rear position opposite to the input port. An organic waste decomposition treatment apparatus characterized in that: (2) Separation slope having a large number of slits or sieves at least on a part of the bottom inclined at the side of the separation / stirring tank, and a decomposed product / granule comprising a vibration mechanism for applying vibration to the separation slope 2. The organic waste decomposition treatment apparatus according to the above item 1, further comprising a stirring medium separation device.

【0006】(3)排出口に設置されたスライド板又は
扉の開口度を調節できる扉開閉機構を備えたことを特徴
とする前項1又は2に記載の有機性廃棄物等の分解処理
装置。 (4)分解物・粒状撹拌媒体分離装置の上方又は下方あ
るいは上方及び下方に、遠赤外ヒーターを設置したこと
を特徴とする前項2又は3のいずれか1項に記載の有機
性廃棄物の分解処理装置。 (5)分解・撹拌槽壁を被包する2重構造のジャケット
と、そのジャケット内に設けた複数の水加熱用ヒーター
とジャケット中の水温を測定する単数個所又は複数個所
に設けられた温度センサーと、温度制御装置とよりなる
分解・撹拌槽の温度調節機構を備えてなることを特徴と
する前項1ないし4のいずれか1項に記載の有機性廃棄
物等の分解処理装置。
(3) An apparatus for decomposing organic waste or the like as described in (1) or (2) above, further comprising a door opening / closing mechanism capable of adjusting an opening degree of a slide plate or a door provided at the discharge port. (4) The organic waste according to any one of (2) to (3) above, wherein a far-infrared heater is installed above, below, or above and below the decomposition product / granular stirring medium separation device. Disassembly equipment. (5) A jacket having a double structure enclosing the wall of the disassembling / stirring tank, a plurality of heaters for water heating provided in the jacket, and a temperature sensor provided at one or more places for measuring the water temperature in the jacket. 5. The decomposition apparatus for decomposing organic waste as described in any one of the above items 1 to 4, further comprising a temperature control mechanism for a decomposition / stirring tank comprising a temperature control device.

【0007】(6)横置きドラム型分解・撹拌槽の内部
に充填される粒状撹拌媒体が、粒径の異なるものの組合
せであることを特徴とする前項1〜5のいずれか1項に
記載の有機性廃棄物等の分解処理装置。 (7)横置きドラム型分解・撹拌槽内の投入口付近では
平均粒度が比較的大径の粒状撹拌媒体が存在し、被処理
物排出口付近では比較的平均粒度が小径の粒状撹拌媒体
が存在してなることを特徴とする前項1ないし6のいず
れか1項に記載の有機性廃棄物等の分解処理装置。 (8)分解・撹拌槽の内部に回転可能に略水平に配設さ
れた回転シャフトと、この回転シャフトに軸方向の複数
箇所に仮想螺旋状に突設された撹拌棒と、各撹拌棒に付
設された撹拌子とからなる撹拌機構を備えたことを特徴
とする前項1ないし7のいずれか1項に記載の有機性廃
棄物等の分解処理装置。 (9)槽壁又は槽底に設けた吸気又は吹き込み口から循
環雰囲気ガス又は空気を分解・撹拌槽に導入する分解・
撹拌槽の雰囲気調整機構を設けたことを特徴とする前項
1ないし8のいずれか1項に記載の有機性廃棄物等の分
解処理装置。 (10)槽壁又は槽底に設けた吸気又は吹き込み口から
循環雰囲気ガス又は空気を分解・撹拌槽に導入する分解
・撹拌槽の雰囲気調整機構を設け、さらに前記循環雰囲
気ガス系又は空気系に水分凝縮装置又は浄化装置を設け
たことを特徴とする前項1ないし9のいずれか1項に記
載の有機性廃棄物等の分解処理装置。 (11)横置きドラム型分解・撹拌槽の内部に充填され
る粒状撹拌媒体が、多孔質のセラミック球、特に多孔質
壁の中空セラミック球であることを特徴とする前項1な
いし9のいずれか1項に記載の有機性廃棄物等の分解処
理装置。
(6) The granular stirring medium filled in the horizontal drum type disassembling / stirring tank is a combination of those having different particle diameters. Decomposition equipment for organic waste. (7) There is a granular stirring medium having a relatively large average particle diameter near the inlet in the horizontal drum type disassembling / stirring tank, and a granular stirring medium having a relatively small average particle diameter near the discharge port of the workpiece. 7. The apparatus for decomposing organic waste or the like according to any one of the above items 1 to 6, wherein the apparatus is present. (8) A rotating shaft rotatably disposed substantially horizontally inside the disassembling / stirring tank, a stirrer rod projecting at a plurality of positions in the axial direction of the rotary shaft in a virtual spiral shape, and a stirrer. 8. The apparatus for decomposing organic waste or the like according to any one of items 1 to 7, further comprising a stirring mechanism including an attached stirrer. (9) Decomposition to introduce the circulating atmosphere gas or air into the agitation tank from the intake or blowing port provided on the tank wall or bottom.
9. The apparatus for decomposing organic waste or the like according to any one of Items 1 to 8, further comprising an atmosphere adjusting mechanism for the stirring tank. (10) An atmosphere adjusting mechanism for the decomposition / stirring tank for introducing the circulating atmosphere gas or air into the decomposition / stirring tank through an intake or blowing port provided on the tank wall or the bottom of the tank is provided. 10. The apparatus for decomposing organic waste or the like according to any one of the items 1 to 9, further comprising a water condensing device or a purifying device. (11) The granular stirring medium filled in the horizontal drum type disassembly / stirring tank is a porous ceramic sphere, particularly a hollow ceramic sphere having a porous wall. An apparatus for decomposing organic waste or the like according to claim 1.

【0008】[0008]

【発明の実施の形態】次ぎに本発明の実施の形態につい
て図面を参照して説明する。図1は本発明実施例装置の
説明断面図、図2は同装置説明正面図、図3は本発明実
施例装置で用いた粒状撹拌媒体の一部切欠外観図、図4
は本発明実施例装置の内部状態説明図である。図5は他
の実施例装置の正面図である。図中、1は有機性廃棄
物、2は粒状撹拌媒体、3は分解・撹拌槽、4は撹拌機
構、5は空気調和手段、6加熱手段、ヒーター、9は投
入口、12は粒状撹拌媒体微細連通孔、13は粒状撹拌
媒体微細凹凸表面、14は分解物、処理済み物、15は
排出口、18は収納箱、19は遠赤外ヒーター、16は
網目篩又は多孔部、17は乾燥粒状撹拌媒体戻し管、2
0は電動篩機、21は乾燥粒状撹拌媒体戻し羽根、22
は撹拌棒、23は撹拌子、24は位置調節シリンダー又
は角度調節機構、25は開閉扉又はダンパーである。本
発明は装置を横置処理槽とし、槽内撹拌機を、対応する
ほぼ水平横方向軸とし、新しい撹拌棒構造、形状、配置
とした。処理すべき有機廃棄物の投入口は一端に近い位
置とし他端に近い位置に処理済製品又は分解物の取り出
し口位置を設ける。槽には内部を加熱する加熱手段であ
るヒーター6と空気又は調整雰囲気を通気する雰囲気調
和手段5を設ける。排気は循環してもよく乾燥や微生物
分解の場合には有害物を除去し水蒸気を必要程度に調整
して還流することができる。この場合には臭気、有害物
除去装置は小型化できる利点があり熱回収と利用が容易
になる。有害物除去には紫外線分解、光・チタン酸化物
分解・オゾン分解、活性炭等炭素質吸着剤が利用でき
る。加熱又は熱回収のために分解・撹拌層底部及び外側
面を2重にして内部に水を充填する。水加熱用耐蝕性ヒ
ーター6で加熱するとともに分解・撹拌層内部3で発生
する発酵・分解熱を熱交換し、収納保存する。粒状撹拌
媒体2は例えばセラミック類の略球状物、角のある片あ
るいは角がとれた形状の転動する細片、その表面部の微
細凹凸面13と内部に多数の連通ポアー(孔)12を有
し、その微細凹凸表面部13及びポアー12の内表面に
有機性廃棄物等の分解用微生物を育成するとともに有機
性廃棄物1が排出する過剰の水分を一時的に吸収保存
し、放出し、同時に有機性廃棄物を磨砕しつつ速やかに
好気性に導き菌を植え付ける。嫌気条件でも同様に促進
する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Next, embodiments of the present invention will be described with reference to the drawings. 1 is an explanatory cross-sectional view of an apparatus according to an embodiment of the present invention, FIG. 2 is a front view illustrating the apparatus, FIG. 3 is a partially cutaway external view of a granular stirring medium used in the apparatus according to an embodiment of the present invention, and FIG.
FIG. 4 is an explanatory diagram of an internal state of the device according to the embodiment of the present invention. FIG. 5 is a front view of another embodiment device. In the figure, 1 is an organic waste, 2 is a granular stirring medium, 3 is a decomposition / stirring tank, 4 is a stirring mechanism, 5 is an air conditioning means, 6 heating means, a heater, 9 is an inlet, and 12 is a granular stirring medium. Fine communication holes, 13 is a fine irregular surface of the granular stirring medium, 14 is a decomposition product, a processed product, 15 is an outlet, 18 is a storage box, 19 is a far-infrared heater, 16 is a mesh sieve or a porous portion, and 17 is a drying unit. Granular stirring medium return pipe, 2
0 is an electric sieve, 21 is a dry granular stirring medium return blade, 22
Is a stirring rod, 23 is a stirring bar, 24 is a position adjusting cylinder or an angle adjusting mechanism, and 25 is an opening / closing door or a damper. In the present invention, the apparatus is a horizontal processing tank, the stirrer in the tank is a corresponding substantially horizontal transverse axis, and a new stirring rod structure, shape, and arrangement are adopted. The inlet of the organic waste to be treated is located at a position near one end, and a take-out position of the treated product or decomposition product is provided at a position near the other end. The tank is provided with a heater 6 as a heating means for heating the inside and an atmosphere conditioning means 5 for ventilating air or a regulated atmosphere. The exhaust gas may be circulated, and in the case of drying or microbial decomposition, harmful substances can be removed and steam can be adjusted to a necessary degree and refluxed. In this case, the odor and harmful substance removing device has an advantage that it can be miniaturized, and heat recovery and utilization become easy. For the removal of harmful substances, ultraviolet light decomposition, light / titanium oxide decomposition / ozone decomposition, and carbonaceous adsorbents such as activated carbon can be used. For heating or heat recovery, the inside of the decomposition / stirred layer and the outer surface are doubled and filled with water. The fermentation / decomposition heat generated inside the decomposition / stirring layer 3 is exchanged by heating with the corrosion-resistant heater 6 for water heating and stored and stored. The granular stirring medium 2 includes, for example, substantially spherical ceramics, angular pieces or rolling small pieces having sharp corners, a fine uneven surface 13 on the surface thereof, and a large number of communication pores (holes) 12 therein. In addition, the microorganisms for decomposing organic waste and the like are grown on the fine uneven surface portion 13 and the inner surface of the pore 12, and the excess water discharged from the organic waste 1 is temporarily absorbed and stored and released. At the same time, the organic waste is rapidly aerobicized while grinding the organic waste, and the bacteria are inoculated. It promotes anaerobic conditions as well.

【0009】撹拌機構4の撹拌運動と硬質有孔性粒状撹
拌媒体により摩擦で微細化され、さらに好気性微生物の
活動により堆肥、ミネラル有効成分を含む分解物14が
生成する。粒状撹拌媒体及び分解物14は所定の撹拌運
動と空気調和手段、加熱媒体により乾燥し撹拌軸の軸方
向に、大きいものから小さいものに分級される条件があ
ることを発見した。この性質によって比較的乾燥し微細
な分解物14と粒状撹拌媒体2は生の比較的粗大な有機
性廃棄物等から分離した帯域を形成し、乾燥しつつ投入
口9の反対側に設けた排出口15から少しづつ制限的に
連続的に取り出すことができた。半連続的又は回分的操
作も可能で、同様に槽内に帯域形成ができた。分解物は
一時的に大量には取り出さず分離収納機構8の網目状篩
又は多孔板部16で粒状撹拌媒体2を分離し、分解物4
は篩下として収納箱18に落下し、粒状体撹拌媒体2は
戻し管又は樋を通過して分解撹拌槽に戻される。分離機
構には乾燥を補助する赤外線又は遠赤外線ヒーター19
と、送りと分離を加速する振動機20を配設する。ヒー
ターは電動篩との相乗効果で網の目詰まりを防止する。
また空気調和の吸気の一部を網下から網目を潜って少量
取り入れると一層分離効果と目詰まり防止効果を増進す
る。網上を向流に流す気流も乾燥に有効である。加熱殺
菌と冷却もできる。空気調和又は雰囲気調整手段5から
の排気は脱臭機構7で脱臭の後、排気ブロアー25を通
過して大気に放出する。排気に含まれる水分は結露の形
で脱臭機構7又は間接冷却手段で回収される。寒冷地で
は水槽の保温に利用できる。排気循環の場合には雰囲気
ガス還流配管又は空気還流配管を付設する。
[0009] The fine particles are finely divided by friction by the stirring movement of the stirring mechanism 4 and the hard porous granular stirring medium, and the decomposition products 14 containing compost and mineral effective components are generated by the activity of the aerobic microorganisms. It has been found that the granular stirring medium and the decomposition product 14 are dried by a predetermined stirring motion, air conditioning means, and a heating medium, and are classified into large to small ones in the axial direction of the stirring shaft. Due to this property, the relatively dry and fine decomposition product 14 and the granular stirring medium 2 form a zone separated from raw relatively coarse organic waste and the like. From the outlet 15, it was possible to take it out continuously in a limited manner. Semi-continuous or batch operation was also possible, and a zone could be formed in the tank as well. The decomposition product is not temporarily taken out in large amounts, and the granular stirring medium 2 is separated by the mesh sieve or the perforated plate portion 16 of the separation and storage mechanism 8, and the decomposition product 4
Falls below the sieve into the storage box 18, and the granular material stirring medium 2 is returned to the decomposition stirring tank through a return pipe or a gutter. An infrared or far infrared heater 19 for assisting drying is provided in the separation mechanism.
Then, the vibrator 20 for accelerating the feeding and the separation is provided. The heater prevents mesh clogging in synergy with the electric sieve.
In addition, if a part of the air-conditioning intake air is taken under the mesh from below the mesh and taken in a small amount, the separating effect and the clogging preventing effect are further enhanced. An air current flowing countercurrently on the net is also effective for drying. Heat sterilization and cooling are also possible. The exhaust air from the air conditioning or atmosphere adjusting means 5 is deodorized by the deodorizing mechanism 7 and then passes through the exhaust blower 25 and is discharged to the atmosphere. Moisture contained in the exhaust gas is collected by the deodorizing mechanism 7 or indirect cooling means in the form of condensation. In cold regions, it can be used to keep water tanks warm. In the case of exhaust circulation, an atmosphere gas recirculation pipe or an air recirculation pipe is provided.

【0010】本発明の1つの特徴である撹拌による分級
と良好な雰囲気ガス雰囲気又は好気性雰囲気の維持は撹
拌棒の配置と撹拌子作用、取り出し口が槽底より高位置
にあり制御が容易なためと推測される。実験により分解
槽内雰囲気と分解物分離性能を付与する配置を定めるこ
とができる。撹拌棒の位置を螺旋状、多条螺旋状又は比
較的接近した干渉位置に配置し、したがって撹拌子の位
置も相当した配置になることにより機能が異なる処理帯
域が構成できた。撹拌子は例えば細長状で棒又は短冊状
板を並べ、格子状、又はフォーク状で撹拌棒先端を加工
したものであってもよい。撹拌棒は間隔を保った撹拌子
を移動している。このようにすると撹拌効果、撹拌子の
剪断効果、擂り潰し効果、分級効果等が働いて、混合物
中の塊、粒の移動が水分、粒度、比重により異なった粉
砕と分離、菌の作用を起す。この条件は槽内の軸方向位
置、高さ方向位置によって堆積圧、粒度、物質分布があ
るので効果が異なることによる。先行する撹拌棒と撹拌
子が粒状撹拌媒体群への有機廃物等の押しつけ、かき分
けで破砕力と磨砕力、或る種の篩分が同時に各処理帯域
特に投入口付近帯域で強く働く。この粗砕と磨砕作用は
ボールミルの磨砕作用とは異なっている。さらに軽量、
軟質の木材チップの作用とも異なっている。
One of the features of the present invention, classification by stirring and maintenance of a good atmosphere gas atmosphere or aerobic atmosphere are easy to control because of the arrangement of the stirring rod, the action of the stirrer, and the take-out port being located higher than the bottom of the tank. It is supposed to be. Experiments can determine the atmosphere in the decomposition tank and the arrangement for imparting the decomposition product separation performance. By setting the position of the stirring rod in a spiral shape, a multi-spiral shape, or a relatively close interference position, and thus the position of the stirrer is also correspondingly arranged, processing zones having different functions can be configured. The stirrer may be, for example, an elongated bar or strip-shaped plate arranged and processed into a lattice or fork shape with the tip of the stirrer rod processed. The stir bar is moving the stir bar at a certain interval. In this way, the stirring effect, the shearing effect of the stirrer, the crushing effect, the classifying effect, etc. work, and the movement of the lumps and grains in the mixture causes pulverization and separation depending on the moisture, particle size, specific gravity, and the action of bacteria. . This condition is based on the fact that the effect differs depending on the deposition pressure, particle size, and material distribution depending on the axial position and height position in the tank. The preceding stirring rod and stirrer press the organic waste and the like against the group of granular stirring media, and the crushing force and the crushing force, as well as certain sieving, simultaneously act strongly in each treatment zone, particularly in the zone near the inlet, by separating. The crushing and grinding actions are different from those of a ball mill. Even lighter,
It also differs from the action of soft wood chips.

【0011】加えて掻き上げられた粒状撹拌媒体が転動
移動する場所ではボールミルとしても作用する。間隔を
置いた格子状又は重層板状あるいは篩状の撹拌子は乾燥
細粒を比重分離、粒度分離しつつ掻き上げ、斜面落下に
より出口側へ移動させ、重い湿細粒には篩分け沈下作用
と掻き上げ乾燥作用を伴いつつ通路堆積層を部分的に疎
にし、粒度分離を起こしつつ移動して細粒は上に移動し
粗粒は横又は下にこぼれて沈下し、細粒は浮上し出口側
へ崩れるように移動し、仮想的螺旋線又は食い違い位置
にある撹拌子が作る疎な部分に落下し、追随位置の撹拌
子は先行する撹拌子が形成した疎な部分に混合物を押し
込む、この時に軽い粒子は浮き、水分が比較的多く、比
較的粗い重い粒子は沈み、浮き上がった粒子は追随した
撹拌子が作った空洞又は疎な部分へと傾斜を斜めに落ち
る。この動作を繰り返して結果的に粒度分布と分離を構
成できたものと推察される。疎密交替、移動と転動の繰
り返しは、また切り返し動作として空気又は雰囲気と混
合物の接触を良好にし、層全体を空気雰囲気では好気性
に維持する。脱臭や有害物除去では雰囲気あるいは雰囲
気添加物例えば中和剤との接触を良好にする。掻き上げ
と粒度、比重分離で出口高さに浮き上がった乾燥小粒子
に富む分解物部分が排出され粒状撹拌媒体分離が円滑に
なる。このような分級的処理法はこれまで知られていな
かったものである。したがって比較的短い軸方向長さで
帯域を構成し生に近い有機廃棄物と微生物処理乾燥品の
分離を容易にしたものである。
In addition, in a place where the scraped-up granular stirring medium rolls and moves, it also functions as a ball mill. A grid-like, multi-layer plate or sieve-like stirrer is used to separate dry granules with specific gravity, separate particles and scrape them up. The sedimentary layer is partially sparsely scattered with the drying action, moving while causing particle size separation, fine grains move up, coarse grains spill down or down, and fine grains float. It moves so as to collapse to the exit side, falls on a sparse part created by a stirrer at a virtual spiral line or a staggered position, and the stirrer at the following position pushes the mixture into the sparse part formed by the preceding stirrer, At this time, the light particles float, the water content is relatively high, the relatively coarse heavy particles sink, and the lifted particles fall diagonally to the cavity or sparse part created by the stirrer that follows. It is presumed that by repeating this operation, the particle size distribution and the separation could be formed as a result. Alternating alternation, movement and rolling are also provided as a switching operation to improve the contact between the air or the atmosphere and the mixture and to keep the entire layer aerobic in an air atmosphere. For deodorization and removal of harmful substances, good contact with the atmosphere or an atmosphere additive such as a neutralizing agent is provided. The decomposed material part rich in dry small particles which has floated to the outlet height by the scraping, the particle size and the specific gravity separation is discharged, and the granular stirring medium is separated smoothly. Such a classification method has not been known before. Therefore, the band is constituted by a relatively short axial length, and the separation of the organic waste and the microorganism-treated dried product which are almost raw is facilitated.

【0012】槽に充填する粒状撹拌媒体は見かけ比重
1.2ないし2.3程度で被処理物より重いものが適当
である、しかし重すぎると被処理物の粗大なものも浮き
上がったり破砕力、磨砕力が低下する。径3mmないし
15mmが重さ、磨砕表面積の点から適しているが少量
の粗大なものが混入していてもよい。しかし大粒径のも
のが多すぎると好気性処理の場合には粒中心部に嫌気性
部分が多く形成され時に異臭の原因になることがある。
逆にこれより微細なものは有機性廃棄物処理品との分離
が困難で望ましくない。粒状撹拌媒体表面は微細な凹凸
面の存在が望ましく微生物の着床が容易であるととも
に、水分吸収面積増大、粗面かつ硬質面により磨砕効果
を上げることができる。粒状体内部表面を形成する連通
ポアー径は平均50ミクロン付近が主である孔径分布が
好ましく大きい内部表面積を持ち水分浸透を促進すると
ともに微生物保持量が大で、しかも繊維性閉塞物の侵入
を防止できる。 孔径が大きすぎると微生物床としての
有効内部表面積が少なくなり、孔径が小さすぎると孔閉
塞しやすくなり吸水、脱水が円滑でなく嫌気性になりや
すく、堆積物の通気性の改善効果が劣ることになる。粒
状撹拌媒体は木材チップ等と異なり粒子密度は有機性廃
棄物より重いものとし撹拌によって槽内で掻き上げられ
たり沈降すると同時に磨砕力を作用させる。自体の摩耗
損失が少ないものが望ましい。
The granular stirring medium to be filled in the tank is suitably an apparent specific gravity of about 1.2 to 2.3 and heavier than the object to be treated. Grinding power decreases. A diameter of 3 mm to 15 mm is suitable in terms of weight and grinding surface area, but a small amount of coarse material may be mixed. However, if there are too many particles having a large particle size, in the case of aerobic treatment, many anaerobic portions are formed at the center of the particles, which sometimes causes an unpleasant odor.
Conversely, finer particles are undesirable because they are difficult to separate from organic waste products. It is desirable that the surface of the granular stirring medium has a fine uneven surface, and it is easy to implant microorganisms, and the grinding effect can be enhanced by an increased water absorption area and a rough and hard surface. The diameter of the communicating pores forming the inner surface of the granular material is preferably around 50 microns on average, and the pore size distribution is preferable. It has a large internal surface area, promotes moisture penetration, has a large amount of microorganisms, and prevents the penetration of fibrous plugs. it can. If the pore size is too large, the effective internal surface area as a microbial bed will be reduced, and if the pore size is too small, the pores are likely to be clogged, water absorption and dehydration will not be smooth and anaerobic, and the effect of improving sediment permeability will be poor. become. The granular agitation medium is different from wood chips and the like in that the particle density is heavier than the organic waste, and is stirred up and settled in the tank by the agitation, and at the same time, exerts a grinding force. It is desirable to have a small wear loss.

【0013】分解物は出口の篩分機構で篩分し、粒状撹
拌媒体は槽に戻すことによって粒状撹拌媒体の損失は大
幅に減じることができる。高強度の粒状撹拌媒体は形態
安定性と大きい破砕効果が製品の細粒化と相まって他の
方式のような補充物の分解物への移行損失による分解物
の無用の増加を避けることができる。本発明では年間1
ないし2回、10%程度の粒状撹拌媒体補充で足り堆肥
又は分解物量は従来法の半分以下にすることができる。
一方、有機質の土壌化の場合には必ずしも硬質である必
要はなく破砕煉瓦あるいはその表面加工物のような適度
の耐水性、多孔性のものでよい。また使用中に適度に摩
耗して転動性と角の破砕性を利用してもよい。材質はア
ルミナ質、粘土質、酸化鉄質等又はガラス質、岩石、火
山灰質で非多孔質の粒状撹拌媒体と多孔質粒状撹拌媒体
を混用してもよい。これらは転動造粒、流動造粒、押し
出し切断、破砕若しくはそれらの併用と焼結又はセメン
ト結合剤によって製造でき、表面強度増加あるいは角と
りのために転動操作、表面焼結を加えることができるが
耐水性若しくは親水性あるいは非撥水性で上記のように
水分が侵入し菌及び生体に対し実質的に毒性がないこと
が必要である。上記性質の多孔性天然物、加工物、破片
等であってもよい。表面剥離後に強度が急低下するもの
は程度により好ましくない。
The decomposition product is sieved by the sieving mechanism at the outlet, and the granular agitation medium can be greatly reduced by returning the granular agitation medium to the tank. The high-strength granular agitation medium, combined with the morphological stability and the great crushing effect, combined with the product refining, can avoid the useless increase of the decomposed product due to the loss of transfer of the supplement to the decomposed product as in other methods. In the present invention, one year
Two or more replenishments of the granular stirring medium of about 10% are sufficient, and the amount of compost or decomposition products can be reduced to less than half that of the conventional method.
On the other hand, in the case of organic soil formation, it is not necessarily required to be hard, and a moderately water-resistant and porous material such as a crushed brick or a surface processed product thereof may be used. In addition, it may be appropriately worn during use to utilize the rolling property and the crushability of the corner. The material may be a mixture of a non-porous granular stirring medium and a porous granular stirring medium of alumina, clay, iron oxide or the like, or vitreous, rock, or volcanic ash. These can be manufactured by tumbling granulation, fluidized granulation, extrusion cutting, crushing or a combination thereof and sintering or cement binder, and it is possible to add tumbling operation and surface sintering to increase surface strength or squaring. It is necessary that it is water-resistant, hydrophilic or non-water-repellent, and that it has substantially no toxicity to bacteria and living organisms, as described above. It may be a porous natural product, processed product, shard, or the like having the above properties. What sharply decreases the strength after surface peeling is not preferable depending on the degree.

【0014】槽内雰囲気調整又は空気調和の通気量は発
生水分を除去し槽内の好気性雰囲気維持のために運転温
度により槽容積1立方メートルあたり0.2ないし10
立方メートルの範囲が適当であり、粒状体1立方メート
ルあたり0.4ないし7立方メートル/分程度がよい。
投入廃棄物の品質、量、製品状況、運転温度によって低
温から比較的高温まで容易に条件を定めることができ
る。槽内部温度は菌の活動が活発である15℃以上80
℃以下で、25ないし50℃で特に45℃付近が好適で
ある。この場合には複数種類の菌が同時作用する特徴を
利用するものである。60℃付近以上では低温殺菌温度
になり、それ以上80℃付近までは耐熱性菌を必要とす
る。
The atmosphere in the tank or the air-conditioning air flow rate is 0.2 to 10 per cubic meter of the tank volume depending on the operating temperature in order to remove generated moisture and maintain an aerobic atmosphere in the tank.
The range of cubic meters is appropriate, and it is preferably about 0.4 to 7 cubic meters / minute per cubic meter of the granular material.
Conditions can be easily set from low to relatively high depending on the quality, quantity, product status, and operating temperature of the input waste. The temperature inside the tank should be higher than 15 ° C and the activity of bacteria is 80
C. or lower, preferably 25 to 50.degree. C., particularly around 45.degree. In this case, a feature in which a plurality of types of bacteria act simultaneously is used. When the temperature is around 60 ° C. or higher, the pasteurization temperature is reached.

【0015】本発明の装置の最も著しい特色は15℃な
いし45℃付近において操作する時に発揮される。すな
わち木材チップ、おがくず等の補充倍地を使用する分解
物排出口で分離しない従来型に比し有機性廃棄物の制約
が少なく空気又は循環ガス供給によって雰囲気調整又は
好気性の槽内空気調和を行うためである。これによって
微生物にとって過剰の水分、アンモニア等の窒素化合物
を槽から速やかに追い出して微生物繁殖を促進し有機物
分解を加速し、有機性廃棄物の組成制約を少なくするも
のである。このようにして投入後2時間で細粒状にな
り、24時間で乾燥残渣量10ないし15%収率で堆
肥、飼料になる。土壌菌、生体にも好適な性質になる。
The most striking feature of the device of the present invention is exhibited when operating at around 15 ° C to 45 ° C. In other words, compared with the conventional type that does not separate at the decomposition product discharge port that uses a replenishing material such as wood chips, sawdust, etc., there is less restriction on organic waste and air or circulating gas supply to adjust the atmosphere or aerobic air conditioning in the tank. To do it. Thus, excessive moisture and nitrogen compounds such as ammonia are quickly expelled from the tank to promote the growth of microorganisms, accelerate the decomposition of organic substances, and reduce the compositional restrictions of organic wastes. In this way, it becomes fine granules 2 hours after the introduction, and becomes compost and feed with a dry residue amount of 10 to 15% in 24 hours. It has properties suitable for soil bacteria and living organisms.

【0016】ジャケット内の水は槽内に軸方向、上下方
向の粒度分布、物質分布を付けたことによる発熱の著し
い部分から熱のジャケット又は水槽への伝熱、撹拌子に
よる掻取伝熱で除熱し、また乾燥熱によって熱不足にな
る部位に熱を供給し熱交換乾燥を促進して、適度の温度
分布又は均一化をはかり局部的過熱、冷却等を防止す
る。過剰の熱は空気調和によって系外へ乾燥熱として除
く。良好な操作条件又は発酵条件維持のために複数の水
加熱用ヒーター6と水槽及び槽内の複数箇所の温度セン
サー28による測定、調節が好ましく、設定温度を分布
させると熱対流により熱交換を促進できる。有機性廃棄
物等被処理物の組成、水分、品質、投入量、投入速度、
外気温度、雰囲気ガス又は空気温度、循環ガス量、処理
成績を測定、勘案しつつ容易に製品品質と歩留を管理が
できる。雰囲気ガスは燃焼排ガス、炭酸ガス、窒素、時
に還元性ガス、中和剤、オゾン等添加ガスであり得る。
[0016] The water in the jacket is obtained by transferring heat from a remarkably heated portion to the jacket or the water tank due to the particle size distribution and material distribution in the axial direction and the vertical direction in the tank, and heat transfer by scraping by the stirrer. Heat is removed, and heat is supplied to a portion where the heat becomes insufficient due to the drying heat to promote heat exchange drying, thereby achieving appropriate temperature distribution or uniformity to prevent local overheating and cooling. Excess heat is removed as drying heat out of the system by air conditioning. In order to maintain good operating conditions or fermentation conditions, it is preferable to measure and adjust by using a plurality of heaters 6 for heating water and temperature sensors 28 in a water tank and a plurality of points in the tank. When a set temperature is distributed, heat exchange is promoted by heat convection. it can. The composition, moisture, quality, input amount, input speed,
Product quality and yield can be easily controlled while measuring and considering the outside air temperature, atmospheric gas or air temperature, circulating gas amount, and processing results. The atmosphere gas may be combustion exhaust gas, carbon dioxide gas, nitrogen, and sometimes an additional gas such as a reducing gas, a neutralizing agent, and ozone.

【0017】図1において投入口9から投入した有機性
廃棄物等は撹拌子23を取り付けた撹拌棒(連結棒)2
2で槽内にある粒状撹拌媒体2を分解中の有機性廃棄物
と入り口部で混合、破砕、磨砕、加温し、過剰水分を調
整し発酵を開始・進行させる。撹拌子は連結棒先端に取
り付け又は撹拌棒の先端加工によってもよい。撹拌軸に
平行な底部と壁面を掻きとれる位置に撹拌子の先端があ
る。 送り翼、押し戻し翼又は堰を組合わせ併用しても
よく上下、縦横方向に粒度分布、物質分布を付けること
ができる。装置条件は試験によって決めることができ
る。発酵又は乾燥、除害終了した分解物と粒状撹拌媒体
の混合物は出口である排出口15から必要により位置調
節シリンダー又は角度調節機構24で開閉扉又はダンパ
ー25を調節して流出量を調整しつつ電動篩機20に排
出され、過熱しないように連続的に樋に流しつつ遠赤外
ヒーター19で好ましくは温度調節しつつ照射し効率よ
く製品、篩面に熱を与え残留湿分を乾燥し、付着目詰ま
りを防止しつつ篩分し、乾燥粒状撹拌媒体を戻し管1
7、戻し羽根21を経て分解・撹拌槽3の投入側に戻
す。この乾燥粒状撹拌媒体は有機性廃棄物の水分を急速
に吸収調整できる。分離した分解物は収納箱18に収納
する。遠赤外ヒーターの過熱防止用又は加熱殺菌用に温
度調節、電動篩機電源の連動回路設置は分解物変質防止
のために望ましい。
In FIG. 1, the organic waste or the like introduced from the inlet 9 is a stirring rod (connecting rod) 2 provided with a stirring bar 23.
In step 2, the granular stirring medium 2 in the tank is mixed with the organic waste being decomposed at the entrance, mixed, crushed, crushed, and heated to adjust the excess water to start and advance fermentation. The stirrer may be attached to the tip of the connecting rod or by processing the tip of the stirring rod. The tip of the stirrer is located where the bottom and wall parallel to the stirring axis can be scraped off. A feed wing, a push-back wing or a weir may be used in combination, and a particle size distribution and a material distribution can be provided in the vertical and horizontal directions. Equipment conditions can be determined by testing. The mixture of the decomposed product and the granular stirring medium, which has been fermented or dried and eliminated, is adjusted from the discharge port 15 as an outlet by adjusting the opening / closing door or the damper 25 with the position adjusting cylinder or the angle adjusting mechanism 24 as necessary to adjust the amount of the outflow. It is discharged to the electric sieving machine 20, and it irradiates by irradiating while controlling the temperature preferably by the far-infrared heater 19 while continuously flowing down the gutter so as not to overheat. The mixture is sieved while preventing clogging, and the dried granular stirring medium is returned to the pipe 1
7. Return to the input side of the decomposition / stirring tank 3 via the return blade 21. This dry granular agitation medium can rapidly absorb and control the water content of the organic waste. The separated decomposition product is stored in the storage box 18. It is desirable to control the temperature to prevent overheating of the far-infrared heater or to sterilize by heating, and to install an interlocking circuit for the power supply of the electric sieving machine in order to prevent degradation of the decomposition products.

【0018】図4において分解・撹拌槽3内の高低分布
については水分が多く、粗大な有機性廃棄物の投入口9
を堆積高が高くても投入できるように比較的高い位置に
設けている。取り出し口15は高い位置又は任意高さに
設け、複数投入口、取り出し口を設けてもよい。取り出
し・篩分け機能は高さと傾斜調節可能にすると便利であ
る。有機廃棄物処理では投入口からの投入物は低位に転
動落下して粒状撹拌媒体群に巻き込まれて順次破砕、脱
水、発酵して多孔化・軽量化し、出口側へ押し出されて
発酵を継続しつつ移動し出口付近で発酵を終了して乾燥
細粒化する。乾燥又は有害物脱離操作でも同様にでき
る。図3は粒状撹拌媒体の例で球状で表面が硬質の多孔
媒体2の表面の微細凹凸面13表面模式図と粒表面13
の部分断面と内部の部分断面のポアー群12の模式図部
分で粉粒焼結体では迷路状の連通多孔性物質であり得
る。排出口側堆積高の槽内分布では斜面は堆積物表面更
新によって空気又は雰囲気調和、乾燥を促進し、混合帯
域の構成は品質の均一化に役立つ。本発明によれば、新
しい撹拌機構造、分解物取り出し・分離と微生物保持性
粒状撹拌媒体による磨砕・圧潰作用、分離の複合作用及
び水槽の熱授受、雰囲気調整又は空気調整、分解物取り
出し位置、給排気位置選択等の組み合わせと最適温度の
維持によって発酵、有害物除去等を促進し、処理時間を
短縮し、しかも分解目的によっては粒状撹拌媒体材質は
高強度のアルミナ質だけでなく比重が重いものならば粘
土その他の土質、灰、煉瓦片等の広範囲から選択でき
る。
In FIG. 4, the high and low distribution in the decomposition / stirring tank 3 has a large amount of water and the coarse organic waste input port 9 is large.
Is provided at a relatively high position so that it can be charged even if the deposition height is high. The outlet 15 may be provided at a high position or at an arbitrary height, and a plurality of inlets and outlets may be provided. It is convenient to make the removal and sieving function adjustable in height and tilt. In organic waste treatment, the input material from the inlet is rolled down to a low level, and is caught in the group of granular stirring media, crushed, dehydrated, and fermented to make it porous and lightweight, and pushed out to the outlet side to continue fermentation The fermentation is finished near the outlet to dry and granulate. Drying or removal of harmful substances can be similarly performed. FIG. 3 shows an example of a granular agitation medium.
In the schematic diagram of the pore group 12 of the partial cross-section and the internal partial cross-section, the granular sintered body may be a maze-like communicating porous substance. In the distribution of the deposit height at the outlet side, the slope promotes air or atmosphere conditioning and drying by renewing the deposit surface, and the composition of the mixing zone contributes to uniform quality. According to the present invention, a new stirrer structure, a combined effect of grinding and crushing action by a granular stirring medium for taking out / separating decomposed matter and a microorganism-retaining particulate stirring medium, heat transfer of a water tank, atmosphere adjustment or air conditioning, decomposed matter taking out position , Fermentation, removal of harmful substances, etc. are promoted by the combination of selection of supply / exhaust position, etc. and maintenance of the optimum temperature, and the processing time is shortened. If it is heavy, it can be selected from a wide range such as clay or other soil, ash, brick pieces and the like.

【0019】[0019]

【実施例】実施例1:幅2.7m,奥行、高さとも1.
3mの装置において、生ゴミ(水分平均80%)を日量
100キログラム処理した。投入後2ないし3時間で生
ゴミ原形はなくなり、菌の混入、活動開始を促進できる
ことがわかった。4ないし5時間で加熱熱源不要となり
10時間で消化が終了する。必要によって24時間かけ
て余熱によって乾燥度を高めることができる。槽温度4
0℃、常温付近で活性の菌を使用し、撹拌機回転数2.
4回/分、吸引換気量最大5.6立方メートル/分で
3.5立方メートル/分程度に設定した。粒状撹拌媒体
はアルミナ粉を転動造粒した径3ないし9mmが90%
の球状焼結体で空隙率15%平均孔径は50ミクロン
で、700リットルを充填し、連続撹拌しつつ調理生ゴ
ミを投入した時、約50キログラムずつ朝晩投入し昼夜
連続運転できた。一時に100キログラム投入しても差
し支えなかった。歩留は有機廃棄物の質と堆肥又は飼
料、肥効土壌化減量等、目的によって、3ないし15%
の範囲で調整できた。腐敗臭、生ゴミ臭がない水分8な
いし20%の乾燥物が得られた。生ゴミの成分、配合物
としての籾殻、藁等の混入の場合も堆肥、園芸土壌改良
剤、飼料混入物として利用できるものが得られた。排気
の異臭は少なく特に排気循環をすると脱臭が容易であっ
た。最大電力は3.3キロワットであった。150日運
転後にセラミック性粒状撹拌媒体入れ替えなしで10%
補充だけで運転継続できた。生ゴミ成分は処理能力に殆
ど無関係で調整の必要はなかった。30キログラム/日
の小型装置も同様な成績であった。水槽外側に循環排気
の風箱を設けることができ、保温と水分凝縮、給気加温
と寒冷地における運転を可能にする。煉瓦質破片、礫、
酸化鉄還元ペレットも粒状撹拌媒体として単独又は混合
使用できた。
EXAMPLES Example 1: Width 2.7m, depth, height 1.
In a 3 m apparatus, garbage (moisture average: 80%) was treated at a daily dose of 100 kg. It was found that the raw garbage disappeared within 2 to 3 hours after the introduction, and that the contamination of bacteria and the start of the activity could be promoted. The heating heat source becomes unnecessary in 4 to 5 hours, and the digestion is completed in 10 hours. If necessary, the degree of drying can be increased by residual heat over 24 hours. Bath temperature 4
Using bacteria active at 0 ° C. and around normal temperature, the number of rotation of the stirrer is 2.
The rate was set to about 3.5 cubic meters / minute at a rate of 5.6 cubic meters / minute at a maximum of 5.6 cubic meters / minute. The granulated agitation medium is 90% of 3 to 9 mm in diameter by rolling granulation of alumina powder.
The spherical sintered body was 15% in porosity and had an average pore diameter of 50 microns, and was filled with 700 liters. When cooked garbage was charged with continuous stirring, about 50 kilograms were charged in the morning and night, and continuous operation could be performed day and night. It was safe to throw in 100 kilograms at a time. Yield is 3 to 15% depending on the purpose such as the quality of organic waste and compost or feed, reduction of fertilized soil, etc.
Could be adjusted within the range. A dried product having a water content of 8 to 20% without rotting odor and garbage odor was obtained. In the case of mixing of raw garbage components and rice husks and straw as a compound, those which can be used as compost, horticultural soil conditioner, and feed contaminants were obtained. Deodorization of the exhaust gas was small, and deodorization was easy particularly when the exhaust gas was circulated. The maximum power was 3.3 kW. 10% after 150 days of operation without replacing the ceramic granular stirring medium
Operation could be continued with only replenishment. The garbage component was almost irrelevant to the treatment capacity and did not need to be adjusted. A small device at 30 kilograms / day performed similarly. A wind box for circulating exhaust can be provided outside the water tank to enable heat retention and moisture condensation, supply air heating and operation in cold regions. Brick debris, gravel,
Iron oxide reduced pellets could also be used alone or as a mixture as a granular stirring medium.

【0020】(対照例):無機粒状撹拌媒体を使用しな
い在来型の単純撹拌、籾殻、おがくず、木材片等を菌母
材として加える混入式では数時間から数日間生ゴミ原形
をとどめている場合があった。また在来型では添加母材
は1ないし2か月に1回入れ替えが必要で堆肥として2
0ないし30%歩留であり減量率は悪く単純乾燥と変ら
ない場合もあった。処理可能の生ゴミ成分も制約があ
り、蛋白質過剰では運転が難かしかった。例えば野菜ゴ
ミ10に対し魚等の窒素質ゴミ0.5ないし3と適当な
範囲があった。熱源、動力は100キログラム/日処理
で最大7キロワット×24時間必要であった。アルミナ
質球形撹拌媒体を使用して底部掃除口に多孔板分離機能
を付け、排出試験した。未分解物の閉塞が激しく、目皿
破損も認められた。
(Comparative example): In the conventional simple stirring method using no inorganic granular stirring medium, the mixed type in which rice hulls, sawdust, wood chips and the like are added as a fungal base material, the raw garbage remains for several hours to several days. There was a case. In addition, in the conventional type, the added base material needs to be replaced once every one to two months.
The yield was 0 to 30%, and the rate of weight loss was poor. There are also restrictions on the garbage components that can be treated, and operation was difficult with excess protein. For example, for vegetable garbage 10, there was an appropriate range of 0.5 to 3 for nitrogenous garbage such as fish. The heat source and power required a maximum of 7 kilowatts x 24 hours at 100 kilograms / day treatment. A perforated plate separation function was attached to the bottom cleaning port using an alumina-based spherical stirring medium, and an emission test was performed. The undecomposed material was severely clogged and the perforated plate was broken.

【0021】実施例2:実施例1の装置で有機性臭気汚
泥である水路汚泥、埋め立て地泥土を生ゴミと混合し、
それぞれ実施例1同様に処理し無臭の土状物が得られ
た。
Example 2 The apparatus of Example 1 is used to mix organic odorous sludge, i.e., channel sludge and landfill mud, with garbage,
Each was treated in the same manner as in Example 1 to obtain an odorless earth-like material.

【0022】[0022]

【発明の効果】本発明装置によれば、魚、野菜その他の
生ゴミ等の有機性廃棄物の分解処理を簡単な処理操作で
大幅減容のもとに達成できる。有機性廃棄物の分解物は
堆肥、土壌肥効成分から飼料まで用途、処分先を広くで
き、減容率も高く、有害物を含む土壌等の処理も容易に
できる。
According to the apparatus of the present invention, the decomposition treatment of organic waste such as fish, vegetables and other garbage can be achieved by a simple treatment operation while greatly reducing the volume. The decomposition products of organic wastes can be used in a wide range of applications and disposal destinations from compost and soil fertilizing components to feeds, have a high volume reduction rate, and can easily treat soil containing harmful substances.

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

【図1】本発明実施例装置の説明断面図。FIG. 1 is an explanatory sectional view of an apparatus according to an embodiment of the present invention.

【図2】同装置の説明正面図。FIG. 2 is an explanatory front view of the device.

【図3】本発明実施例装置で用いた粒状撹拌媒体の部分
切欠外観図。
FIG. 3 is a partially cutaway external view of a granular stirring medium used in the apparatus of the embodiment of the present invention.

【図4】本発明実施例装置の内部状態説明図。FIG. 4 is an explanatory diagram of an internal state of the apparatus according to the embodiment of the present invention.

【図5】本発明の他の実施例装置の正面図。FIG. 5 is a front view of a device according to another embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1…有機性廃棄物、2…粒状撹拌媒体、3…分解・撹拌
槽、4…撹拌機構、5…空気調和手段、6加熱手段、ヒ
ーター 9…投入口、12…粒状撹拌媒体微細連通孔、13…粒
状撹拌媒体微細凹凸表面、14…分解物、処理済み物、
15…分解物排出口、18…収納箱、19…遠赤外ヒー
ター、16…網目篩又は多孔部、17…乾燥粒状撹拌媒
体戻し管、20…電動篩機、21…乾燥粒状撹拌媒体戻
し羽根、22…撹拌棒、23…撹拌子、24…位置調節
シリンダー又は角度調節機構、25…開閉扉又はダンパ
ー、26…駆動機、27、28…温度センサー、29…
振動用モーター。
DESCRIPTION OF SYMBOLS 1 ... Organic waste, 2 ... Granular stirring medium, 3 ... Decomposition / stirring tank, 4 ... Stirring mechanism, 5 ... Air conditioning means, 6 heating means, heater 9 ... Input port, 12 ... Fine communication hole of granular stirring medium, 13: Granular stirring medium fine uneven surface, 14: Decomposed product, treated product,
15: Decomposed product discharge port, 18: Storage box, 19: Far infrared heater, 16: Mesh sieve or porous part, 17: Dry granular stirring medium return pipe, 20: Electric sieve machine, 21: Dry granular stirring medium return blade , 22: stirring rod, 23: stirring bar, 24: position adjusting cylinder or angle adjusting mechanism, 25: opening / closing door or damper, 26: driving machine, 27, 28: temperature sensor, 29 ...
Vibration motor.

Claims (11)

【特許請求の範囲】[Claims] 【請求項1】装置内部の横置ドラム型の分解・撹拌槽の
前方上部に開口された有機性廃棄物等の投入口を有し、
その分解・撹拌槽内には横貫して設置された回転シャフ
トと、その回転シャフトに垂設された複数の撹拌棒から
なる撹拌機構を有し、また分解・撹拌槽の壁面には排出
口を有し、さらに分解・撹拌槽内には微生物が着生した
粒状撹拌媒体が充填され、かつ装置側面又は後部には開
口された排気口、その排気口より脱臭装置を介して排気
ブロアーにつながる雰囲気調節機構を備えた有機性廃棄
物を微生物分解処理又は微生物分解処理及び乾燥処理す
る有機性廃棄物の分解処理装置において、前記横置ドラ
ム型の分解・撹拌槽内の前記粒状撹拌媒体及び分解物を
取り出す排出口が前記投入口に対置した後方の位置に設
置してなることを特徴とする有機性廃棄物の分解処理装
置。
An inlet for organic waste and the like which is opened at an upper front part of a horizontal drum type disassembling / stirring tank inside the apparatus;
The disassembly / stirring tank has a stirring mechanism consisting of a rotating shaft installed transversely and a plurality of stirring rods suspended from the rotating shaft. An atmosphere in which a granular stirring medium on which microorganisms have settled is filled in the decomposition / stirring tank, and an exhaust port is opened on the side or rear of the apparatus, and the exhaust port is connected to an exhaust blower through a deodorizing device. An organic waste decomposition treatment apparatus comprising a control mechanism and a microorganism decomposition treatment or a microorganism decomposition treatment and a drying treatment for organic waste, wherein the granular stirring medium and the decomposition product in the horizontal drum type decomposition / stirring tank are provided. An organic waste decomposition treatment apparatus, wherein a discharge port for taking out the waste is provided at a position rearward opposite to the input port.
【請求項2】分離・撹拌槽の側部に斜設された少なくと
も底部の一部に多数のスリット又は篩い目を有する分離
用スロープ、及び同分離用スロープに振動を与える振動
機構よりなる分解物・粒状撹拌媒体分離装置を備えたこ
とを特徴とする請求項1に記載の有機性廃棄物の分解処
理装置。
2. A decomposed product comprising a separating slope having a large number of slits or sieves at least at a part of a bottom portion inclined at a side portion of a separating / stirring tank, and a vibration mechanism for applying vibration to the separating slope. The organic waste decomposition treatment apparatus according to claim 1, further comprising a granular stirring medium separation apparatus.
【請求項3】排出口に設置されたスライド板又は扉の開
口度を調節できる扉開閉機構を備えたことを特徴とする
請求項1又は2に記載の有機性廃棄物等の分解処理装
置。
3. The apparatus for decomposing organic waste or the like according to claim 1, further comprising a door opening / closing mechanism capable of adjusting an opening degree of a slide plate or a door provided at the discharge port.
【請求項4】分解物・粒状撹拌媒体分離装置の上方又は
下方あるいは上方及び下方に、遠赤外ヒーターを設置し
たことを特徴とする請求項2又は3のいずれか1項に記
載の有機性廃棄物の分解処理装置。
4. The organic matter according to claim 2, wherein a far-infrared heater is provided above, below, above or below and above the decomposition product / granular stirring medium separation device. Waste decomposition equipment.
【請求項5】分解・撹拌槽壁を被包する2重構造のジャ
ケットと、そのジャケット内に設けた複数の水加熱用ヒ
ーターとジャケット中の水温を測定する単数個所又は複
数個所に設けられた温度センサーと、温度制御装置とよ
りなる分解・撹拌槽の温度調節機構を備えてなることを
特徴とする請求項1ないし4のいずれか1項に記載の有
機性廃棄物等の分解処理装置。
5. A double-structured jacket for enclosing the wall of a disassembling / stirring tank, a plurality of water heaters provided in the jacket, and a single or a plurality of locations for measuring the water temperature in the jacket. The decomposition treatment apparatus for organic wastes according to any one of claims 1 to 4, further comprising a temperature control mechanism for a decomposition / stirring tank comprising a temperature sensor and a temperature control device.
【請求項6】横置きドラム型分解・撹拌槽の内部に充填
される粒状撹拌媒体が、粒径の異なるものの組合せであ
ることを特徴とする請求項1〜5のいずれか1項に記載
の有機性廃棄物等の分解処理装置。
6. The method according to claim 1, wherein the granular stirring medium filled in the horizontal drum type decomposition / stirring tank is a combination of those having different particle diameters. Decomposition equipment for organic waste.
【請求項7】横置きドラム型分解・撹拌槽内の投入口付
近では平均粒度が比較的大径の粒状撹拌媒体が存在し、
被処理物排出口付近では比較的平均粒度が小径の粒状撹
拌媒体が存在してなることを特徴とする請求項1ないし
6のいずれか1項に記載の有機性廃棄物等の分解処理装
置。
7. A granular stirring medium having a relatively large average particle size is present in the vicinity of a charging port in a horizontal drum type disassembling / stirring tank.
7. The apparatus for decomposing organic waste or the like according to claim 1, wherein a granular stirring medium having a relatively small average particle size is present in the vicinity of the discharge port of the object to be treated.
【請求項8】分解・撹拌槽の内部に回転可能に略水平に
配設された回転シャフトと、この回転シャフトに軸方向
の複数箇所に仮想螺旋状に突設された撹拌棒と、各撹拌
棒に付設された撹拌子とからなる撹拌機構を備えたこと
を特徴とする請求項1ないし7のいずれか1項に記載の
有機性廃棄物等の分解処理装置。
8. A rotatable shaft rotatably disposed substantially horizontally inside a disassembling / stirring tank, a stirrer rod projected at a plurality of positions in the axial direction of the rotatable shaft in a virtual spiral shape, and The apparatus for decomposing organic waste or the like according to any one of claims 1 to 7, further comprising a stirring mechanism including a stirrer attached to the rod.
【請求項9】槽壁又は槽底に設けた吸気又は吹き込み口
から循環雰囲気ガス又は空気を分解・撹拌槽に導入する
分解・撹拌槽の雰囲気調整機構を設けたことを特徴とす
る請求項1ないし8のいずれか1項に記載の有機性廃棄
物等の分解処理装置。
9. An atmosphere adjusting mechanism for a decomposition / stirring tank for introducing a circulating atmosphere gas or air into a decomposition / stirring tank from an intake or a blowing port provided on a tank wall or a tank bottom. An apparatus for decomposing organic waste or the like according to any one of claims 8 to 10.
【請求項10】槽壁又は槽底に設けた吸気又は吹き込み
口から循環雰囲気ガス又は空気を分解・撹拌槽に導入す
る分解・撹拌槽の雰囲気調整機構を設け、さらに前記循
環雰囲気ガス系又は空気系に水分凝縮装置又は浄化装置
を設けたことを特徴とする請求項1ないし9のいずれか
1項に記載の有機性廃棄物等の分解処理装置。
10. A decomposition / stirring tank atmosphere adjusting mechanism for introducing a circulating atmosphere gas or air into a decomposition / stirring tank through an intake or blowing port provided on a tank wall or a tank bottom, and further comprising the circulating atmosphere gas system or air The apparatus for decomposing organic waste or the like according to any one of claims 1 to 9, wherein a water condensing device or a purifying device is provided in the system.
【請求項11】横置きドラム型分解・撹拌槽の内部に充
填される粒状撹拌媒体が、多孔質のセラミック球である
ことを特徴とする請求項1ないし9のいずれか1項に記
載の有機性廃棄物等の分解処理装置。
11. The organic solvent according to claim 1, wherein the granular stirring medium filled in the horizontal drum type decomposition / stirring tank is a porous ceramic sphere. Decomposition equipment for toxic waste.
JP2000403099A 2000-12-28 2000-12-28 Organic waste decomposition treatment equipment Expired - Fee Related JP3624832B2 (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006305501A (en) * 2005-04-28 2006-11-09 Universal Line Kk Organic waste treatment apparatus
CN109365479A (en) * 2018-11-12 2019-02-22 吉林建筑大学 A kind of agricultural wastes circulation comprehensive utilizes system
CN114751797A (en) * 2022-05-31 2022-07-15 山东聚义兴生物工程有限公司 Method for rapidly preparing fertilizer from cage-rearing chicken manure by utilizing decomposition technology

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105272431A (en) * 2015-10-23 2016-01-27 卢润湖 Organic waste treatment equipment

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006305501A (en) * 2005-04-28 2006-11-09 Universal Line Kk Organic waste treatment apparatus
JP4701351B2 (en) * 2005-04-28 2011-06-15 国立大学法人岐阜大学 Organic waste treatment equipment
CN109365479A (en) * 2018-11-12 2019-02-22 吉林建筑大学 A kind of agricultural wastes circulation comprehensive utilizes system
CN114751797A (en) * 2022-05-31 2022-07-15 山东聚义兴生物工程有限公司 Method for rapidly preparing fertilizer from cage-rearing chicken manure by utilizing decomposition technology

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