JPS58223680A - Fermentation composting treatment device - Google Patents

Fermentation composting treatment device

Info

Publication number
JPS58223680A
JPS58223680A JP57102695A JP10269582A JPS58223680A JP S58223680 A JPS58223680 A JP S58223680A JP 57102695 A JP57102695 A JP 57102695A JP 10269582 A JP10269582 A JP 10269582A JP S58223680 A JPS58223680 A JP S58223680A
Authority
JP
Japan
Prior art keywords
fermentation
composting
dehydration
base
bed
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
JP57102695A
Other languages
Japanese (ja)
Other versions
JPS6131045B2 (en
Inventor
達也 内田
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.)
Resonac Corp
Original Assignee
Hitachi Chemical Co Ltd
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 Hitachi Chemical Co Ltd filed Critical Hitachi Chemical Co Ltd
Priority to JP57102695A priority Critical patent/JPS58223680A/en
Publication of JPS58223680A publication Critical patent/JPS58223680A/en
Publication of JPS6131045B2 publication Critical patent/JPS6131045B2/ja
Granted 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Landscapes

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

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 不発明に有機性の廃棄物、特に一般家庭や飲食業、旅鮪
莱から生じる生ゴミや中/ト規摸の下水処理場から排出
さnる余剰汚泥の発酵堆肥化処理装置外に関する。水分
を多量に・含み、腐敗し易く悪臭音発生する生ゴミや汚
泥に、一般的に地方自治体や専門処理業者により収集さ
tL多額の費用1[する坤立や焼却法で処分さ1してき
たが、その性質上、近年微生wJ(1)生物化学的酸化
分解反応を利用した発酵堆肥化処理法か見直さnて実用
化さnつつある。発酵堆肥化処理法の条件としてr1%
涼科廃棄物の含水率の調整や酸化分解反応と発酵ガス置
換に必要な空気の供給か必要とさjLるか、入量の収集
式nる生ゴミには、水分か多量に含まnる他非発酵性、
離発醇性のガ2ス、木材、プラスチック、紙咎り混入か
多く、脱水や選別、粉砕等(IJ前処理工程全必要とし
、また脱離反出水υ対策V(も多額の股偏費を賛すとい
う問題点かありた。一方前述の一般家庭や飲食業等から
(/J規楔の小さいlA果物堆肥化処理の揚台に、比較
的選別し易い利点かめる反面、処理量の笈wJか人きく
季節的な外気幅の影響全党は易く安定した処理を行えl
い久点かめった。例えば牢にを気の流通孔を供11面や
底面に設けたの与の装置で、水分の多い生ゴミ忙投入し
続けると、槽下部から汚水が浸出すると同時に槽内に嫌
気化し、内容物に腐敗臭を発生す4. v J)−7’
xらr1却って不衛生な蚊、ハエ等O発生源となる可能
性かある。不発明にこ几らυ背#Oを十分考慮し生ゴミ
、汚泥Vの壱磯性島来物ケ一つりコンパクトな装置で経
済的、衛生的にかつ短時間で発酵堆肥化処理を行い、乾
いた取り扱い易い有機質の土壌改良材等にする装kを提
供す/bものである0 本発明に」二部に投入口を基底部に落下口會南する竪型
槽内の投入口下部に回転脱水装置JLを設り、脱水装匝
勿除く槽内壁IHJを発酵堆肥化床と721、、更に槽
内ガスυ強制排出装にヶ設けたこと紮特徴とする発酵堆
肥化処理装置に関する。
[Detailed Description of the Invention] The present invention relates to the fermentation and composting of organic waste, particularly kitchen garbage generated from households, food and beverage businesses, and tuna raisins, and surplus sludge discharged from medium/high-grade sewage treatment plants. Regarding outside the processing device. Garbage and sludge that contain large amounts of moisture, are easily putrefied, and emit foul odors and noises are generally collected by local governments or specialized disposal companies and disposed of using disposal methods or incineration methods, which cost a large amount of money. However, due to its nature, in recent years, fermentation and composting treatment methods that utilize microbial wJ(1) biochemical oxidation and decomposition reactions have been reviewed and are being put into practical use. r1% as a condition for fermentation composting treatment method
It is necessary to adjust the water content of coolant waste and to supply the air necessary for oxidative decomposition reactions and fermentation gas replacement. Others non-fermentable,
There is a lot of contamination with expelled gas, wood, plastic, and paper, and dehydration, sorting, and pulverization (all IJ pretreatment processes are required), and countermeasures against desorption and water release (V) also require a large amount of unbalanced costs. On the other hand, from the above-mentioned general households and food and beverage businesses, etc. (/J) Although the small wedge size of the IA fruit composting table has the advantage of being relatively easy to sort, on the other hand, the amount of processing is too low. The influence of the seasonal outside air range makes it easy for all parties to perform stable processing.
It took a long time. For example, if a cell is equipped with air circulation holes on the surface or the bottom of the cell, and if you continue to feed garbage with a high moisture content, the waste water will seep out from the bottom of the cell, and at the same time the tank will become anaerobic, causing the contents to become anaerobic. 4. Generates a putrid odor. v J)-7'
On the contrary, it may become a source of unsanitary O such as mosquitoes and flies. With due consideration to the uninventive Niko et al υ back #O, we can economically, hygienically, and quickly ferment and compost food waste and sludge using a single, compact device. To provide a dry and easy-to-handle organic soil conditioner, etc., the present invention provides a system for making dry and easy-to-handle organic soil conditioners. The present invention relates to a fermentation and composting processing apparatus which is equipped with a rotary dewatering device JL, a dehydration device, a sludge removing tank inner wall IHJ, a fermentation and composting bed 721, and a tank internal gas υ forced discharge device.

不発明による有機性廃棄物の発酵堆肥化処理装置に、発
酵堆肥の諸条件を満足させる以下の諸機構を同−装置内
に組み込み、こnらの機構か有機的に働くことに裏り処
理量の変ルD、気温変wJV?−も対処でき、維持管[
も衛生的に容易にできるという特長を備える。即ち、原
料有機性廃棄性廃棄物の含水率調整材ケ不袋Vr−する
か。
The following mechanisms that satisfy the various conditions of fermentation compost are incorporated into the uninvented fermentation and composting equipment for organic waste, and these mechanisms work organically. Quantity change le D, temperature change wJV? − can also be dealt with, maintenance tube [
It also has the advantage of being hygienic and easy to use. That is, whether the moisture content adjustment material of the raw organic waste is used as a waste bag or not.

極めて少量にできる(口)転脱水装w、、堆肥化床を常
時好気的に維持し、かつ発酵ガス中に含まnろ水分を除
去する九めの槽内ガスの強制排装置か同−装置内に組み
込まnてい番か。以下本発明を図面の実施例に従い、説
明する。第1図に1不発明の概略的栴成をボ丁因である
0不装匣に、1の上部発酵幅と2QJ基底部からなる竪
型槽↓9成る◎土部発酵槽1に、倣かト力V(広がる円
錐形とlし、上部中央部VL生ゴミaυ投入口5を設け
、投入時以外に蓋4 Vtエク略密閉状態と1丁。発酵
+v11t;I〜f熱壁とすることが望ましい05に投
入′j′る午ゴミり分割賂nlこ朱軟lツノイドである
。竪型槽に上部発酵槽と基底部に分割−Cき上部発#檜
0基&部に対し水平に回転できるLうvLfLっている
o6t/、L発酵借を中心軸に幻し水平に基鳳部2上で
回転塾せるための回転用把手であり発酵槽内金に股りた
攬件板/の作用で後述の堆肥化床14の攪拌を行う。
A dewatering device that can be used in an extremely small amount, and a forced exhaust device for the gas in the tank that maintains the composting bed aerobically at all times and removes the moisture contained in the fermentation gas. Is it installed in the device? The present invention will be described below with reference to embodiments shown in the drawings. Fig. 1 shows the schematic construction of 1. A vertical tank consisting of 1. upper fermentation width and 2.QJ base ↓ 9. Kato force V (spreading conical shape, VL raw garbage aυ input port 5 is provided in the upper center part, lid 4 Vt is almost sealed state except when charging. Fermentation + V11t; I ~ f heat wall It is preferable to divide the waste into a vertical tank and divide it into an upper fermenter and a base. It is a rotating handle that can be rotated horizontally on the main part 2, with the L fermentation plate as the central axis, and is a mounting board that is mounted on the inside of the fermenter. The composting bed 14, which will be described later, is stirred by the action of /.

尚、撹拌叡μ数枚に分割しでも良く、又、棒状でもよい
0発酵僧門e?−rユカ5城都2りほば甲人Il/J投
入ロ50王都rコ基底部よυ乱+k R)況水都紮設け
、発膨佃壁との低都空聞を晃停堆肥化床14となす0脱
水部1.j、二に構造となりで291外部にに、不透水
拐買より戚ゐ円筒外弘8ケ銭け、内部にに、上部に多孔
性の回転脱水用ノくスクット9を設けである0バスケツ
ト9に基底部下部に収納さ12次回転用動力10に工9
所定時間回転し7生ゴミ等の脱水及び剥離を行う。この
バスケット9の回転軸と外筒壁との空間に、脱水汚水の
流下路とし、底部エフ装置外へ分離汚水bl排出する0
更にバスケット及び回転軸の中心部にrt、基底部下部
より連通して垂直方向に上下する昇降軸11と昇降用動
力12會設けである。仁の昇降軸11に、バスケット9
内に装置する耐腐食性材質エフなり、柔軟な網状の脱水
容器15に係わり脱水時に下降した定位置にあるが、脱
水完了後、上昇し脱水容器を反転させて内容物の生ゴミ
等を剥離し発酵堆肥床14に落下させる。昇降用動力に
、モーター回転による昇降でも良いか、他に水圧、油圧
、空気圧等を用い上下運動させることもできる〇又、攪
拌のための回転に、基底部盆回転しても良く又1発酵槽
を外部から動力で回転しても良い0更に発酵槽内壁のみ
ならず、基底部上面VL攪拌捧、板等設けても良い。生
ゴミ寺の投入から脱水、剥離、攪拌時の動作QJ概概略
ケシ2図第5図、第4区VC示す。第2図a勺枳性廃莱
物の投入状態、第6図をユ回転脱水状恕、第4図15脱
水後、廃粱吻の剥離の状態囚である。回転脱水器に第5
図で示す如く、バスケット9自身奮多孔性容話となし内
部に脱水容器(/、I鯨腐を不要とz−rこともできる
が、そり廃り(μ内!+5り伯降軸11の上端Sを脱水
バスケットの直径エフわずかに小さくした御し出し板と
1−にとが望ましい◇この場@に、昇降4!11111
の動作耽回葡短かくすることかでき心0 以上QJ##工程を経又堆肥床V(岳下し、攪拌6tし
た脱水生ゴミ等に急速に発酪會開’Anしs発酵分解作
用r(伴9尭齢熱VCより生ゴミ寺の水分か蒸散し、乾
燥か行なわノしる。この蒸散した妬r祥ガス中の水分に
、+M内忙上昇し耐却農オじこ献緬し、書び発rIj、
堆肥を湿間ちせるlこめ、丸酵惜内でかつ堆肥化床の土
部を同V?−発酵ガス吸引116を設け1発酵排ガスC
をbb気ソノアン1フ外部に排出する0この排気vLよ
り、堆肥化床底面に設け7を落下口15から新鮮な空気
ρ3槽内に流入し、堆肥化床を好気的に保ちかつ発酵分
解作用を促進する0又落下口15は底面の適当な位av
t複数個、円形若くはスリット状で設けである・基底部
の一部にtr1通気孔15と対応させて生成堆肥の貯留
ff1l18751設けら扛ており数ケ月に一度の生成
堆肥の排出を行うdl 19に取出口、20に取出とび
らである。18の貯留部にな、通気孔24を設ける。常
時、含水率の商い生ゴミ等の処理を行う際には、この生
成堆肥dを再び5の投入口より堆肥化床14に戻すか。
In addition, the stirring plate may be divided into several pieces, or it may be in the form of a stick. -r Yuka 5 Castle 2 Rihoba Koujin Il/J Insertion Ro 50 Royal capital r Co base +k R) Setting up a state water city, composting a low city space with an expansion Tsukuda wall 0 dewatering section with floor 14 1. J, secondly, the structure is 291, and the outside is a cylindrical shell 8 that is similar to the water-impermeable part, and the inside is equipped with a porous rotary dewatering screw 9 on the top.0 Basket 9 The power for the 12th rotation stored in the lower part of the base 10 and the power 9
It rotates for a predetermined period of time to dehydrate and peel off garbage, etc. The space between the rotating shaft of the basket 9 and the outer cylinder wall is used as a flow path for dehydrated sewage, and the separated sewage bl is discharged to the outside of the bottom F device.
Furthermore, an elevating shaft 11 and an elevating power source 12 are provided at the center of the basket and the rotating shaft, communicating with each other from the lower part of the base and moving up and down in the vertical direction. Basket 9 on the lift axis 11
The corrosion-resistant material installed inside the flexible mesh dehydration container 15 is in a fixed position that lowers during dehydration, but after dehydration is completed, it rises and inverts the dehydration container to peel off the contents such as garbage. and fall onto the fermented compost bed 14. The power for raising and lowering may be a motor rotation, or water pressure, hydraulic pressure, air pressure, etc. may be used for vertical movement. Also, the base tray may be rotated for stirring. The tank may be rotated by power from the outside.Furthermore, not only the inner wall of the fermenter but also the top surface of the base may be provided with a VL stirring bar, a plate, etc. Operations from inputting garbage to dehydration, peeling, and stirring QJ Outline Poppy Figure 2 Figure 5, Section 4 VC is shown. Fig. 2a shows the state in which the waste material is put in, Fig. 6 shows the state in which it is rotated and dehydrated, and Fig. 4 shows the state in which the waste material is peeled off after dehydration. 5th rotary dehydrator
As shown in the figure, the basket 9 itself is porous and there is no dehydration container inside (/, I do not need whale rot. It is preferable to use a push plate with S slightly smaller in diameter of the dehydration basket and 1-nito.
The operation of the process can be shortened and the fermentation and decomposition effect can be rapidly developed on the dehydrated raw garbage, which has been lowered to the compost bed and stirred for 6 tons. (From the 9th grade heat VC, the water in the garbage temple evaporates and is dried.The moisture in this evaporated gas causes +M to rise, and the agricultural waste is evaporated. and write rIj,
Is it possible to dampen the compost in the same way as in the fermentation room and in the soil part of the composting bed? - Provide fermentation gas suction 116 1 fermentation exhaust gas C
From this exhaust VL, fresh air flows into the tank from the drop port 15 provided at the bottom of the composting bed, keeping the composting bed aerobic and fermenting and decomposing it. The zero or drop opening 15 that promotes the action is located at an appropriate position av on the bottom surface.
t Multiple pieces, circular or slit-shaped, are provided. A storage ff1l18751 for generated compost is provided in a part of the base corresponding to the tr1 ventilation hole 15, and the generated compost is discharged once every few months. 19 is an outlet, and 20 is an outlet door. A ventilation hole 24 is provided in the reservoir section 18. When processing raw garbage with a low moisture content, the generated compost d is returned to the composting bed 14 through the input port 5.

15の脱水容器に生ゴミ等と一緒に入nて含水率1l1
111整用として用いることもできるO冬期の気温低下
に伴い微生物の発酵分解作用が抑制さjLる場合や、冬
期、長期間生ゴミ等の投入を中止し、処mを短時間で再
開する場合KH槽内基底部111度検出器21t−設け
、所定温度に1で加編する加熱ヒーター22と調節器2
5を設ける0加熱ヒーターに、線状、若く0板状の難燃
性。
Put it in a dehydration container of No. 15 together with garbage etc. and the water content is 1l1.
111 Can also be used for cleaning purposes When the fermentation and decomposition action of microorganisms is suppressed due to the temperature drop in winter, or when disposing of food waste, etc. is stopped for a long period of time in winter and disposal is restarted in a short time. A detector 21t is provided at the base 111 in the KH tank, and a heating heater 22 and a regulator 2 are provided to adjust the temperature to a predetermined temperature.
5 is provided for the 0 heating heater, with linear, young and plate-like flame retardant properties.

耐熱性のヒーターを用い基底部に埋め込んだジ、基底部
上面に敷設する0加熱ヒーター22に必ずしも心安とし
ないか上記理由の他、岨って大魚の水分を堆肥化床に直
接投入した場合り嫌気状態を除くのに有効である。尚、
投入口5に、生ゴミ等投入時以外に蓋4を常時しておき
、略密閉状態とし通気に下Sから行lわtLるL9にす
る。又通排気方法としてIrx、低部から強制的に送気
し上部より排気する方法もあるが発酵槽を光分密閉状態
にする必9!があり臭気の副γL等も懸念さnるため不
発明の吸引方式が望ましい。
In addition to the above-mentioned reasons, there may be cases where water from large fish is directly poured into the composting bed. Effective in eliminating anaerobic conditions. still,
A lid 4 is kept on the input port 5 at all times except when putting in raw garbage, etc., so that it is in a substantially sealed state and ventilation is performed from the bottom S to L9. Also, as a ventilation method, there is an Irx method, or a method of forcing air from the bottom and exhausting from the top, but it is necessary to keep the fermenter in a light-tight state! Since there is a concern about the odor of secondary γL, etc., the uninvented suction method is desirable.

活性汚泥等の有機性汚泥を不装置で処理する場合に、脱
水バスケット内に自動供給できる配管とポンプ等の装置
を設は脱水装置と全自動的に連動させることかできる0
この場合、汚泥の流入前に予め、凝集剤等?混入丁nは
更に脱水が有効である。脱水バスケットに被脱水対象物
である有機性廃棄物を投入し、投入ロ蓋ケ閉めた後、脱
水装置j/Lか所に時間運転爆tした後、昇降軸か脱水
容器の反転のため所定位置まで上昇し容器中の内容物を
飛散させ次後再び所定位置まで下降し次いで脱水装置か
停止する工程か全自動で行なえる制御装m’i備えnは
本装置を自動化連転することもできる。
When treating organic sludge such as activated sludge without equipment, equipment such as piping and pumps that can automatically feed into the dewatering basket can be installed and linked fully automatically with the dewatering equipment.
In this case, use a flocculant, etc. before the sludge flows in. It is also effective to dehydrate the mixed cloves. After putting the organic waste to be dehydrated into the dehydration basket, and closing the loading slot lid, place the dehydrator in the J/L position for a certain period of time, and then turn the lifting shaft or the dehydration container to the specified position. The device is equipped with a control system that can perform the process of raising the container to a fully automatic position, scattering the contents in the container, and then lowering it again to a predetermined position and then stopping the dehydration device. can.

以上、述べた様に発明の装rtは、発酵堆肥化処理条件
を満足させる諸機構を同一装置内に有機的に組み込んだ
結果、選別し易い中小規模排出源で短期間に衛生的に有
機性廃棄物か処理で@るという効果を得ることか出来る
As mentioned above, as a result of organically incorporating various mechanisms that satisfy the fermentation and composting processing conditions into the same device, the RT system of the present invention is able to hygienically produce organic waste in a short period of time from small and medium-sized emission sources that are easy to sort. It is possible to obtain the effect of waste disposal.

jlわち脱水装置を装置内部に設けたことで原廃棄物に
付随し、又は包合さ7Lる水分會除くことVLLり、含
水率調整材を不敬とするか、大幅に低下できる◎紹未的
に、同一処理量のもとでに、装置堆肥化容積を縮少でき
、かつ生成堆肥も取り扱い易い含水率の低いものか得ら
nる。
In other words, by installing a dehydration device inside the device, it is possible to remove 7L of water that accompanies or is included in the raw waste, making it possible to reduce or significantly reduce the moisture content of the material used to adjust the moisture content. Specifically, with the same throughput, the volume of composting equipment can be reduced, and the resulting compost can be easily handled and has a low moisture content.

発酵ガス全内部から外部へ吸引排出できる構造ヅ とし北ため臭気の漏曳かなく排ガス処理か簡単であり、
同時に堆肥化床を好気的に維持できる。
It has a structure that allows the fermentation gas to be sucked and discharged from inside to the outside, so there is no odor leakage and exhaust gas treatment is easy.
At the same time, the composting bed can be maintained aerobically.

脱水後の有機性廃棄物は堆肥化床に落下すると同時に堆
肥化か始まり、更に上部発酵Nを回転させnは既に発#
を開始している堆肥と混合さfLるので発酵時I&1J
が短縮さn装置の縮少化が図nる。
The organic waste after dehydration starts to be composted as soon as it falls onto the composting bed, and the upper fermentation N is rotated so that the N is already generated.
It is mixed with the compost that has started, so during fermentation I & 1J
This will reduce the number of devices required.

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

第1図に本発明の装置QJ概略断面である。 第2図から第4−に回転脱水装置の動作図である。第5
図に他の脱水装置の断面図である。 符号の説明 1 上S発#相    21!、底部 6 投入口      4 投入口蓋 5 投入ガイド    6 回転用把手7 撹拌板  
    8 脱水装置外筒壁9 脱水用バスケット10
  回転用動力11  昇降軸      12  昇
降@動力16  脱水谷皆?      14  発酵
堆肥床15#下口   16  発酵ガス吸引管17 
 排気ファン    18  生成堆肥貯留部19  
取出口      20  取出とひら21  龜度検
出器   22  加熱ヒーター26  ―部器   
  24  通気孔a 生ゴミ b 分離汚水 C発酵排ガス d 生成堆肥 一4″。 第2図
FIG. 1 is a schematic cross-section of the device QJ of the present invention. FIGS. 2 to 4- are operational diagrams of the rotary dewatering device. Fifth
The figure is a sectional view of another dehydration device. Code explanation 1 # phase from upper S 21! , bottom 6 Inlet 4 Inlet cover 5 Insertion guide 6 Rotating handle 7 Stirring plate
8 Dehydration device outer cylinder wall 9 Dehydration basket 10
Power for rotation 11 Lifting shaft 12 Lifting @ Power 16 Demizutani everyone? 14 Fermentation compost bed 15# lower mouth 16 Fermentation gas suction pipe 17
Exhaust fan 18 Generated compost storage section 19
Outlet port 20 Output port 21 Tension detector 22 Heater 26 - Parts
24 Vent a Garbage b Separated sewage C Fermentation exhaust gas d Produced compost - 4''. Figure 2

Claims (1)

【特許請求の範囲】 1、上部に投入口を基底部に落下口を有する堅型佃内の
投入口下部に回転脱水装置を設け、脱水装置を除く槽内
9間を発酵堆肥化床となし、更に僧門ガスの強制排出装
置t1に設けたC脱眉可能な上部発酵僧と基底部とに分
割さn上郡発#債か基底部に対し水平に回転可能な構造
であるとともに、脱水装置か基底部のほぼ申央位Itり
投入口に対応する位litに直立せしめた構造である特
許請求の範囲第1項記載の発酵堆肥化処理装置。 3、 回転脱水装置tが、内S回転脱水部と外筒壁とて
構成さn1内部回転脱水部にa1基底部げ に垂直でかつ回転可能な軸を設ヰ、この軸の上端に多数
の小孔冬にスリットを壁面VL有する脱水バスケットl
固定するか脱眉自在に設け、外筒部は不透水材貴りり’
zしsがっ基底部に固定し、外筒部内壁と回転軸とり空
間を脱水バスケットでの脱離汚水の流下路とした構造で
ある時rF請求の範囲第1項又は第2項記載の発酵堆肥
化処理装置・ 4、回転脱水装置か、脱水装置内部の脱水バスケット底
部と回転軸の中心部を負通し、垂直方向に上下する昇降
軸VtLり脱水バスケットに脱層可罷に内装する脱水ろ
布又に網状の脱水容器上反転させる構造て必る特許請求
の範囲第3項記載の発酵堆肥化処理装置。 5、王都発#債か内壁のtlは堆肥化床VC相当する深
さ位置まで借壁に連続又は一部切9欠いた攪拌板を固定
し、発酵債υ回転II?−よシ内部堆肥化床を攪拌する
S造である%ff−1f〜求の範囲第2項、第6項又は
第4項記載の発酵堆肥化装置。 6、基底部の落下口か多数の小孔又にスリットでめり、
楕円ガスの排出装置か堆肥化床上部空間に設けらnた吸
引孔であり、発酵堆肥化処理装置外へ発酵ガス全排出芒
せ、同時に基底部格下口より空気を堆肥化床に流通させ
る構造−ごある時r!f梢求の範囲第1項記載の発酵堆
肥化処理装置。 基 7、 勾織部力11人、劇熱拐質で温度検出益及び制御
装置鼠を備えた面状、父に線状の耐熱、耐火材で機わt
’した発熱ヒーター盆設けた構造である%#’l”Fi
g″i?、υ範囲第1狽記載の発酵堆肥化処理装置。
[Claims] 1. A rotary dewatering device is provided below the inlet in a vertical tank that has an inlet at the top and a fall port at the base, and the nine spaces inside the tank excluding the dehydrator are used as a fermentation composting bed. In addition, the forced exhaust device t1 for gas is divided into an upper part that can be removed and a base part, and has a structure that can be rotated horizontally with respect to the base part, as well as a dehydration device. 2. The fermentation and composting apparatus according to claim 1, wherein the fermentation and composting apparatus has a structure in which the bottom part is located approximately at the center of the base and is erected at a position corresponding to the input port. 3. The rotary dewatering device t is composed of an inner S rotary dehydrator and an outer cylindrical wall, and the n1 internal rotary dehydrater has a rotatable shaft that is perpendicular to the base of the a1, and a large number of small Dehydration basket l with slits in the hole and wall surface VL
It can be fixed or removed freely, and the outer cylinder is made of impermeable material.
Z is fixed to the base part, and the inner wall of the outer cylinder part and the rotating shaft space are used as a flow path for the dewatered wastewater in the dehydration basket. Fermentation and composting processing equipment 4. Dehydration using a rotary dehydration equipment or a dehydration basket inside the dehydration basket with a negative passage between the bottom of the dehydration basket and the center of the rotating shaft, and a lifting shaft VtL that moves up and down in the vertical direction. 4. The fermentation and composting apparatus according to claim 3, wherein the fermentation and composting apparatus has a structure in which the filter cloth or the net-like dehydration container is inverted. 5. For the TL of the inner wall of the royal capital, fix a continuous or partially notched stirring plate to the borrowed wall to a depth corresponding to the composting bed VC, and rotate the fermentation bond υ II? - The fermentation composting apparatus according to item 2, item 6, or item 4, which is an S structure in which the internal composting bed is agitated. 6. Insert the slit into the drop opening at the base or the numerous small holes,
It is an elliptical gas discharge device or a suction hole provided in the space above the composting bed, and has a structure that allows all fermentation gas to be discharged outside the fermentation and composting processing device, and at the same time allows air to flow into the composting bed from the lower opening of the base. -Sometimes! f) The fermentation and composting treatment apparatus according to item 1. Group 7, 11 people, Riki Saoribe, a plane with a temperature detection effect and a control device with severe fever, and a wire-shaped heat resistant, fire resistant material.
The structure is equipped with a heating heater tray.
g″i?, υ range No. 1 Fermentation and composting treatment device.
JP57102695A 1982-06-15 1982-06-15 Fermentation composting treatment device Granted JPS58223680A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57102695A JPS58223680A (en) 1982-06-15 1982-06-15 Fermentation composting treatment device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57102695A JPS58223680A (en) 1982-06-15 1982-06-15 Fermentation composting treatment device

Publications (2)

Publication Number Publication Date
JPS58223680A true JPS58223680A (en) 1983-12-26
JPS6131045B2 JPS6131045B2 (en) 1986-07-17

Family

ID=14334387

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57102695A Granted JPS58223680A (en) 1982-06-15 1982-06-15 Fermentation composting treatment device

Country Status (1)

Country Link
JP (1) JPS58223680A (en)

Also Published As

Publication number Publication date
JPS6131045B2 (en) 1986-07-17

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