JP2000317423A - Garbage treatment - Google Patents

Garbage treatment

Info

Publication number
JP2000317423A
JP2000317423A JP12516099A JP12516099A JP2000317423A JP 2000317423 A JP2000317423 A JP 2000317423A JP 12516099 A JP12516099 A JP 12516099A JP 12516099 A JP12516099 A JP 12516099A JP 2000317423 A JP2000317423 A JP 2000317423A
Authority
JP
Japan
Prior art keywords
temperature
ventilation
garbage
fermentation
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
JP12516099A
Other languages
Japanese (ja)
Other versions
JP3504881B2 (en
Inventor
Hirokazu Ishikawa
博一 石川
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.)
ISHIKAWA KIKAI KK
Original Assignee
ISHIKAWA KIKAI 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 ISHIKAWA KIKAI KK filed Critical ISHIKAWA KIKAI KK
Priority to JP12516099A priority Critical patent/JP3504881B2/en
Publication of JP2000317423A publication Critical patent/JP2000317423A/en
Application granted granted Critical
Publication of JP3504881B2 publication Critical patent/JP3504881B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To suppress the fermentation smell in a garbage treatment method for decomposition and annihilation of garbage and to allow the effective utilization of remaining bed material for compost. SOLUTION: In the garbage treatment method for treating the garbage by housing the wooden bed material, such as bark, and the garbage into a treating vessel 1 and treating the garbage by actuating a turning means 2 and a ventilating means 11, the weak turning control to weaken the turning effect by the material turning means 2 and the weak ventilation control to weaken the ventilation of the ventilating means 11 are executed when the temperature in the vessel detected by a temperature sensor 16 is below a set fermentation temperature in a range of 35 to 40 deg.C and the strong turning control to intensify the turning effect by the material turning means 2 and the strong ventilation control to increase the ventilation rate of the ventilating means 11 are executed when the detected temperature in the vessel is below the set fermentation temperature described above, by which the fermentation temperature of the treated material is suppressed within a range of 35 to 40 deg.C.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、生ゴミを分解消滅
させるための生ゴミ処理方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a garbage disposal method for eliminating garbage.

【0002】[0002]

【従来の技術及びその問題点】生ゴミ、例えば調理残滓
や残飯などを分解消滅させるために、処理槽内で適当な
床材と生ゴミとを混合し、発酵させる方法が知られてい
るが、強烈な発酵臭が発散するため、処理槽からの排気
路に消臭装置を接続するなどの対策が採られ、設備コス
トが高くつくばかりでなく、処理槽への生ゴミ投入作業
時に処理槽内から発散する発酵臭が作業者に嫌がられ、
十分に活用されるに至っていないのが実情である。ま
た、使用する床材によっては、処理残滓を堆肥としてそ
のまま活用することができない。
2. Description of the Related Art There is known a method of mixing raw garbage with a proper flooring material in a treatment tank and fermenting the garbage in order to eliminate garbage, for example, cooking residues and garbage. Since strong fermentation odors are emitted, measures such as connecting a deodorizing device to the exhaust path from the treatment tank are taken, which not only increases the equipment cost but also increases the cost of processing garbage into the treatment tank. Workers hate the fermentation odor emanating from inside,
The fact is that it has not been fully utilized. Further, depending on the floor material used, the processing residue cannot be directly used as compost.

【0003】[0003]

【課題を解決するための手段】本発明は上記のような従
来の問題点を解消し得る生ゴミ処理方法を提供すること
を目的とするものであって、その手段を後述する実施形
態の参照符号を付して示すと、処理槽1と、当該処理槽
1内の材料切返し手段2と、槽内温度を検出する温度セ
ンサー16と、槽内に外気を通す通風手段11とを備え
た処理装置を使用し、処理槽1内にバークなどの木質系
床材と生ゴミとを収容し、材料切返し手段2と通風手段
11を作動させて、生ゴミを処理する生ゴミ処理方法で
あって、前記温度センサー16の検出温度が、摂氏35
〜40度の範囲内で設定した設定発酵温度以下のとき
は、材料切返し手段2による切返し作用を弱めた弱切返
し制御と、通風手段11の通風量を少なくした弱通風制
御との内、少なくとも何れか一方の制御を行い、前記検
出温度が前記設定発酵温度以上のときは、材料切返し手
段2による切返し作用を強めた強切返し制御と、通風手
段11の通風量を大きくした強通風制御との内、少なく
とも何れか一方の制御を行うことにより、処理材料の発
酵温度を摂氏35〜40度の範囲内に抑えることを特徴
とする。
SUMMARY OF THE INVENTION An object of the present invention is to provide a garbage disposal method which can solve the above-mentioned conventional problems. In the drawing, a processing tank 1, a material switching means 2 in the processing tank 1, a temperature sensor 16 for detecting a temperature in the tank, and a ventilation means 11 for passing outside air into the tank are provided. A garbage disposal method for treating garbage by using a device, storing wood-based flooring material such as bark and garbage in a treatment tank 1 and operating a material switching means 2 and a ventilation means 11. The temperature detected by the temperature sensor 16 is 35 degrees Celsius.
When the temperature is equal to or lower than the set fermentation temperature set within a range of 4040 ° C., at least one of weak switching control in which the switching operation of the material switching unit 2 is weakened and weak ventilation control in which the ventilation amount of the ventilation unit 11 is reduced. When either of the controls is performed and the detected temperature is equal to or higher than the set fermentation temperature, one of the strong switching control in which the switching action of the material switching means 2 is enhanced and the strong ventilation control in which the ventilation amount of the ventilation means 11 is increased. By performing at least one of the controls, the fermentation temperature of the processing material is suppressed within the range of 35 to 40 degrees Celsius.

【0004】上記本発明方法を実施するについて、具体
的には、前記木質系床材として、バーク堆肥またはバー
ク堆肥を主成分とするものが好適である。また、前記検
出温度が前記設定発酵温度以下のときは、間欠運転され
る材料切返し手段2の駆動時間に対する停止時間の割合
を大きくした弱切返し制御を行うとともに、通風手段1
1の通風量を少なくした弱通風制御とを行い、前記検出
温度が前記設定発酵温度以上のときは、間欠運転される
材料切返し手段2の駆動時間に対する停止時間の割合を
小さくした強切返し制御を行うとともに、通風手段の通
風量を大きくした強通風制御とを行うことができる。
[0004] In carrying out the method of the present invention, specifically, bark compost or bark compost as a main component is preferable as the wood-based flooring material. Further, when the detected temperature is equal to or lower than the set fermentation temperature, the weak switching control in which the ratio of the stop time to the driving time of the intermittently operated material switching means 2 is increased, and the ventilation means 1
(1) weak ventilation control in which the amount of ventilation is reduced, and when the detected temperature is equal to or higher than the set fermentation temperature, strong switching control in which the ratio of the stop time to the driving time of the material switching means 2 that is intermittently operated is reduced. At the same time, it is possible to perform strong ventilation control in which the ventilation amount of the ventilation means is increased.

【0005】また、槽内雰囲気温度を高めるヒーター1
4を併設し、外気温度または前記検出温度が、摂氏20
度以下に設定された発酵促進開始温度以下のときのみ、
前記ヒーター14を作動させることができる。この場
合、具体的には、外気温度または前記検出温度が、摂氏
10度以下に設定された発酵促進開始温度以下のとき、
前記ヒーター14を作動させ、外気温度または前記検出
温度が、摂氏10〜20度範囲内に設定された発酵促進
終了温度以上のとき、前記ヒーター14を停止させるこ
とができる。また、前記ヒーター14は、前記通風手段
11の槽内への送気路12中に配設することができる。
[0005] A heater 1 for increasing the ambient temperature in the bath is provided.
4 and the outside air temperature or the detected temperature is 20 degrees Celsius.
Only when the temperature is below the fermentation acceleration start temperature set below
The heater 14 can be operated. In this case, specifically, when the outside air temperature or the detected temperature is equal to or lower than the fermentation acceleration start temperature set to 10 degrees Celsius or less,
The heater 14 is operated, and when the outside air temperature or the detected temperature is equal to or higher than the fermentation promotion end temperature set in the range of 10 to 20 degrees Celsius, the heater 14 can be stopped. Further, the heater 14 can be disposed in the air supply path 12 into the tank of the ventilation means 11.

【0006】さらに、前記通風手段11を、槽内への送
気路12と、槽外への排気路13と、当該排気路13中
に配設された送風機15とを有するものとし、処理槽1
の投入口8が開かれている間、前記送風機15の通風を
強に切り換えることができる。
Further, the ventilation means 11 has an air supply path 12 into the tank, an exhaust path 13 to the outside of the tank, and a blower 15 disposed in the exhaust path 13. 1
While the input port 8 is open, the ventilation of the blower 15 can be strongly switched.

【0007】また、前記通風手段11の槽内への送気路
として、槽内底部に外気を送入する送気路27を設ける
こともできる。
[0007] Further, as an air passage of the ventilation means 11 into the tank, an air passage 27 for introducing outside air into the bottom of the tank may be provided.

【0008】[0008]

【発明の実施の形態】以下に本発明の好適実施形態を添
付図に基づいて説明すると、図1及び図2において、1
は処理槽であり、内部に切返し手段2を備えている。こ
の切返し手段2は、水平の回転軸3に小径の右送り用リ
ボンスクリュー4と大径の左送り用リボンスクリュー5
とを支持アーム4a,5aにより同心状に支持させたも
ので、モーター6により回転駆動される。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A preferred embodiment of the present invention will be described below with reference to the accompanying drawings.
Denotes a processing tank, which has a switching means 2 inside. The turning means 2 includes a small-diameter right-feed ribbon screw 4 and a large-diameter left-feed ribbon screw 5 on a horizontal rotating shaft 3.
Are concentrically supported by support arms 4a and 5a, and are rotationally driven by a motor 6.

【0009】処理槽1は、図2に示すように、床材と生
ゴミとの混合物である処理材料の投入最大レベルLより
下側の部分1aが、大径の左送り用リボンスクリュー5
に近接する水平円筒状に形成され、前記レベルLより上
側の部分1bは垂直角筒状に形成されている。そして、
図1に示すように、この垂直角筒状の上側部分1bの上
端を閉じる上壁部1cに、開閉自在な蓋7を備えた投入
口8が設けられ、前記水平円筒状の下側部分1aの一端
(小径の右送り用リボンスクリュー4の送り方向側端
部)に、開閉自在な蓋9を備えた取り出し口10が設け
られている。
As shown in FIG. 2, the processing tank 1 has a large-diameter left-feed ribbon screw 5a in which a portion 1a below the maximum input level L of a processing material, which is a mixture of floor material and garbage, is disposed.
And a portion 1b above the level L is formed in a vertical rectangular tube shape. And
As shown in FIG. 1, an opening 8 provided with an openable / closable lid 7 is provided in an upper wall portion 1c which closes the upper end of the vertical rectangular cylindrical upper portion 1b, and the horizontal cylindrical lower portion 1a is provided. At one end (the end in the feed direction of the small-diameter right-feed ribbon screw 4), there is provided a take-out port 10 having a lid 9 that can be opened and closed.

【0010】11は通風手段であって、処理槽上壁部1
cの一端側に連設された送気路12と、処理槽上壁部1
cの他端側に連設された排気路13と、前記送気路12
内に配設されたヒーター14と、前記排気路13内に配
設された送風機15とから構成されている。
Reference numeral 11 denotes a ventilation means, which is an upper wall portion 1 of the processing tank.
c, an air supply passage 12 connected to one end of the treatment tank,
c, an exhaust path 13 connected to the other end side, and the air supply path 12
And a blower 15 disposed in the exhaust path 13.

【0011】16は処理槽1内の温度を検出する温度セ
ンサー、17は投入口開閉蓋7が開いたことを検出する
リミットスイッチなどの開蓋センサーである。マイクロ
コンピューターやプログラマブルシーケンサーなどから
成る制御装置18は、前記温度センサー16の検出温度
信号や開蓋センサー17からのオンオフ信号などに基づ
いて、切返し手段2の駆動用モーター6を制御するモー
ターコントローラー19、通風手段11の送風機15を
制御するモーターコントローラー20、及び通風手段1
1のヒーター14を制御するヒーターコントローラー2
1などを自動制御する。送風機15を制御するモーター
コントローラー20は、モーターのオンオフだけでな
く、回転数を自在に調整し得るもので、ここでは、入力
信号に応じて高速回転(強風)、中速回転(中風)、及
び低速回転(弱風)に切り換えることができ、その各段
回転数も予め設定しておくことができる。また、制御盤
22には、温度センサー16が検出した槽内温度を表示
する槽内温度表示部23、運転スイッチ24、及び取り
出しスイッチ25を備えている。
Reference numeral 16 denotes a temperature sensor for detecting the temperature in the processing tank 1, and reference numeral 17 denotes a cover opening sensor such as a limit switch for detecting that the inlet opening / closing cover 7 is opened. A control device 18 including a microcomputer, a programmable sequencer, and the like includes a motor controller 19 that controls the drive motor 6 of the switching means 2 based on a temperature signal detected by the temperature sensor 16 and an on / off signal from the lid sensor 17. A motor controller 20 for controlling the blower 15 of the ventilation means 11 and the ventilation means 1
Heater controller 2 for controlling one heater 14
1 etc. are automatically controlled. The motor controller 20 that controls the blower 15 can adjust not only the turning on / off of the motor but also the number of revolutions freely. Here, high-speed rotation (strong wind), medium-speed rotation (medium wind), and It is possible to switch to low-speed rotation (weak wind), and the rotation speed of each stage can be set in advance. Further, the control panel 22 includes a bath temperature display section 23 for displaying the bath temperature detected by the temperature sensor 16, an operation switch 24, and a removal switch 25.

【0012】使用に先立って、制御装置18に記憶設定
された制御プログラムに対し、必要な設定を行う。即
ち、制御装置18に設けられたキーボードなどの入力手
段26を利用して、摂氏10度以下の発酵促進開始温度
T1、摂氏10〜20度の発酵促進終了温度T2、摂氏
25〜35度の弱風切換温度T3、摂氏35〜40度の
定常発酵温度T4、3〜10分の切返し手段駆動時間D
1、10〜60分の切返し手段長停止時間S1、及び2
〜10分の切返し手段短停止時間S2が設定される。例
えば、T1=摂氏5度、T2=摂氏15度、T3=摂氏
30度、T4=摂氏37度、D1=5分、S1=30
分、S2=5分に設定することができる。
Prior to use, necessary settings are made for a control program stored and set in the control device 18. That is, using the input means 26 such as a keyboard provided in the control device 18, the fermentation promotion start temperature T1 of 10 degrees Celsius or less, the fermentation promotion end temperature T2 of 10 to 20 degrees Celsius, and the weakness of 25 to 35 degrees Celsius are used. Wind switching temperature T3, steady fermentation temperature T4 of 35 to 40 degrees Celsius T3, switching means driving time D of 3 to 10 minutes
1, 10 to 60 minutes switching means length stop time S1, and 2
A switching means short stop time S2 of 10 minutes is set. For example, T1 = 5 degrees Celsius, T2 = 15 degrees Celsius, T3 = 30 degrees Celsius, T4 = 37 degrees Celsius, D1 = 5 minutes, S1 = 30
Minute, S2 = 5 minutes.

【0013】使用に際して処理槽1には、バーク(樹
皮)、おが屑、樹木剪定屑の砕片などの木質系の床材と
生ゴミとを投入最大レベルLを越えない範囲で投入す
る。この床材としては、生のバークや樹木剪定屑の砕片
などを使用するよりも、種菌の供給源にもなり且つ通気
性、保湿性が良好で適度に柔らかいバーク堆肥を使用す
るのが好ましく、この場合も、完熟したバーク堆肥単体
ではなく、発酵途中にあるバーク堆肥が望ましい。そし
て、バーク堆肥単体ではなく、生ゴミに対する絡みが良
好なおが屑などの微細な木質砕片とを混合するのが好ま
しく、その混合割合は、体積比でバーク堆肥5〜7(好
ましくは6)に対しおが屑など3〜5(好ましくは4)
程度が好ましい。床材と生ゴミの混合比率は、理想的に
は、投入された生ゴミが次の生ゴミの投入までに略消滅
するように、例えば毎日1回の生ゴミ投入の場合、床材
に対して生ゴミが10%以下(好ましくは6〜8%程
度)となるようにする。換言すれば、1回で処理すべき
生ゴミの量と生ゴミの投入時間間隔に応じて床材の量が
決まるので、この床材と生ゴミとを投入最大レベルLを
越えない範囲で収容し得る容積の処理槽1が必要にな
る。
At the time of use, woody flooring materials such as bark, bark, sawdust, and debris of tree pruning waste and garbage are introduced into the treatment tank 1 within a range not exceeding the maximum input level L. As this flooring, it is preferable to use bark compost which is also a source of inoculum and has good air permeability, good moisture retention and moderately soft, rather than using raw bark or crushed pieces of tree pruning debris, Also in this case, it is desirable to use bark compost which is in the middle of fermentation instead of ripe bark compost alone. It is preferable to mix not only bark compost but also fine wood debris such as sawdust that has good entanglement with garbage, and the mixing ratio is 5 to 7 (preferably 6) by bark compost in volume ratio. 3-5 (preferably 4) such as sawdust
The degree is preferred. Ideally, the mixing ratio of flooring and garbage should be such that the input garbage almost disappears by the next garbage input. The amount of garbage is reduced to 10% or less (preferably about 6 to 8%). In other words, the amount of the floor material is determined according to the amount of the garbage to be processed at one time and the time interval of the garbage, so that the floor material and the garbage are accommodated in a range not exceeding the maximum input level L. A processing tank 1 having a sufficient volume is required.

【0014】次に、上記のように床材と生ゴミとを処理
槽1に収容した生ゴミ処理装置と制御装置18に設定記
憶された制御プログラムとを利用して実行される本発明
の生ゴミ処理方法の一例を、図3のフローチャートに基
づいて説明すると、運転スイッチ24のオン操作によ
り、温度センサー16の検出温度XTと設定温度T1〜
T4とが比較され、検出温度XTが発酵促進開始温度T
1(摂氏5度)以上で弱風切換温度T3(摂氏30度)
以下のときは、モーターコントローラー20を介して通
風手段11の送風機15がオフから弱風オンに切り換え
られるとともに、切返し手段2の駆動用モーター6がモ
ーターコントローラー21を介して、駆動時間D1(5
分)と長停止時間S1(30分)とを繰り返す間欠運転
される。
Next, the garbage disposal apparatus according to the present invention, which is executed using the garbage processing apparatus in which the floor material and the garbage are stored in the processing tank 1 as described above, and the control program set and stored in the control unit 18. An example of the dust disposal method will be described with reference to the flowchart of FIG. 3. When the operation switch 24 is turned on, the detected temperature XT of the temperature sensor 16 and the set temperatures T1 to T1 are set.
T4 and the detected temperature XT is the fermentation acceleration start temperature T
Low wind switching temperature T3 (30 degrees Celsius) at 1 (5 degrees Celsius) or higher
In the following cases, the blower 15 of the ventilation means 11 is switched from off to low on via the motor controller 20, and the driving motor 6 of the switching means 2 is driven via the motor controller 21 for the driving time D1 (5).
) And the long stop time S1 (30 minutes).

【0015】即ち、処理槽1内でリボンスクリュー4,
5が、5分回転して30分停止することを繰り返し、送
風機15の吸気作用により、外気が送気路12から処理
槽1内に送入されるとともに排気路13から排出され
る。従って、処理槽1内の床材と生ゴミとの混合物がリ
ボンスクリュー4,5の回転により切返し攪拌されなが
ら通気され、発酵分解が開始される。
That is, in the processing tank 1, the ribbon screw 4,
5 is repeatedly rotated for 5 minutes and stopped for 30 minutes, and the outside air is fed into the processing tank 1 from the air supply path 12 and discharged from the exhaust path 13 by the suction action of the blower 15. Accordingly, the mixture of the floor material and the garbage in the treatment tank 1 is aerated while being repeatedly stirred by the rotation of the ribbon screws 4 and 5, and the fermentation decomposition is started.

【0016】生ゴミの発酵分解が進むにつれて槽内温度
が上昇するが、温度センサー16の検出温度XTが、弱
風切換温度T3(摂氏30度)以上で定常発酵温度T4
(摂氏37度)以下の範囲に上がると、モーターコント
ローラー20を介して通風手段11の送風機15が弱風
オンから中風オンに切り換えられ、処理槽1内の換気が
促進され、槽内温度の上昇が抑制される。さらに発酵分
解が進んで、温度センサー16の検出温度XTが定常発
酵温度T4(摂氏37度)を越えると、モーターコント
ローラー20を介して通風手段11の送風機15が中風
オンから強風オンに切り換えられるとともに、切返し手
段2の駆動用モーター6がモーターコントローラー21
を介して、駆動時間D1(5分)と短停止時間S2(5
分)とを繰り返す間欠運転に切り換えられる。従って、
処理槽1内の換気がさらに促進されるとともに切返し攪
拌の頻度が高くなって、生ゴミの発酵分解速度が抑制さ
れ、それ以上の温度上昇が抑えられる。生ゴミの発酵分
解により、検出温度XTが下がると、その検出温度に応
じた運転状態に切り換えられることは、図3のフローチ
ャートから明らかである。
As the fermentation decomposition of the garbage proceeds, the temperature in the tank rises. When the temperature XT detected by the temperature sensor 16 is equal to or higher than the weak wind switching temperature T3 (30 degrees Celsius), the steady fermentation temperature T4
(37 degrees Celsius) When the temperature rises to the range below, the blower 15 of the ventilation means 11 is switched from the weak wind ON to the medium wind ON via the motor controller 20, the ventilation in the processing tank 1 is promoted, and the temperature in the tank increases. Is suppressed. When the fermentation decomposition proceeds further and the temperature XT detected by the temperature sensor 16 exceeds the steady fermentation temperature T4 (37 degrees Celsius), the blower 15 of the ventilation means 11 is switched from the medium wind ON to the strong wind ON via the motor controller 20. , The driving motor 6 of the switching means 2 is a motor controller 21
Via the drive time D1 (5 minutes) and the short stop time S2 (5
) Is switched to intermittent operation. Therefore,
Ventilation in the treatment tank 1 is further promoted, and the frequency of the agitation is increased, so that the fermentation decomposition rate of the garbage is suppressed, and the temperature rise is further suppressed. It is clear from the flow chart of FIG. 3 that when the detected temperature XT is lowered due to the fermentation decomposition of garbage, the operating state is switched to the detected temperature.

【0017】上記作用により、生ゴミが発酵分解して、
見掛け上、床材のみが残ったような状態になる。勿論、
床材として使用されているバーク堆肥なども未発酵成分
が発酵分解するとともに、機械的磨滅も生じるので、床
材も若干減容する。この状態で次の生ゴミを投入するの
であるが、生ゴミの投入により検出温度XTが低下する
と、図3のフローチャートから明らかなように、その検
出温度に応じた運転状態に切り換えられ、運転が継続さ
れる。なお、生ゴミを投入する時期は、処理中の生ゴミ
が完全に発酵分解して消滅した以後でなければならない
ことはなく、炭水化物が主となる残飯類が多い場合は、
発酵分解速度が遅いので、多少、未発酵分解の生ゴミが
残った状態で次の生ゴミを投入することになるが、前記
のように床材自体も減容してゆくので、処理槽1内の処
理材料が投入最大レベルLを越えない範囲で生ゴミを適
時投入してゆけば良い。
[0017] By the above action, garbage is fermented and decomposed,
Apparently, only the floor material remains. Of course,
Bark compost and the like used as flooring materials also have unfermented components fermented and decomposed and mechanically abraded. In this state, the next garbage is inserted. When the detected temperature XT decreases due to the input of garbage, the operation state is switched to an operation state corresponding to the detected temperature, as is clear from the flowchart of FIG. To be continued. In addition, it is not necessary to put the raw garbage after the raw garbage being processed is completely fermented and decomposed and disappeared.If there is a large amount of garbage mainly composed of carbohydrates,
Since the fermentation decomposition rate is slow, the next garbage is thrown in with some unfermented decomposition garbage remaining. However, as described above, the floor material itself is reduced in volume. The raw garbage may be charged as appropriate as long as the processing material in the container does not exceed the maximum input level L.

【0018】設置場所が寒冷地である場合や使用時期が
厳寒期である場合など、運転開始時の外気温(槽内温
度)が低く、運転スイッチ24のオン操作時点で検出温
度XTが発酵促進開始温度T1(摂氏5度)以下のとき
は、ヒーターコントローラー21を介して通風手段11
内のヒーター14に通電されるとともに、モーターコン
トローラー20を介して通風手段11の送風機15がオ
フから弱風オンに切り換えられる。この結果、処理槽1
内にヒーター14で加熱された外気が送入され、排気路
13より排気される。この予熱作用により槽内温度が上
昇する。そして、検出温度XTが発酵促進終了温度T2
(摂氏15度)を越えると、ヒーターコントローラー2
1を介してヒーター14に対する通電が断たれ、定常運
転に復帰する。
When the installation location is in a cold region or when the usage period is extremely cold, the outside temperature (temperature in the tank) at the start of operation is low, and when the operation switch 24 is turned on, the detected temperature XT increases the fermentation. When the temperature is equal to or lower than the start temperature T1 (5 degrees Celsius), the ventilation means 11
The heater 14 in the inside is energized, and the blower 15 of the ventilation means 11 is switched from off to weak wind on via the motor controller 20. As a result, processing tank 1
The outside air heated by the heater 14 is fed into the inside, and is exhausted from the exhaust path 13. This preheating action raises the temperature in the tank. The detected temperature XT is the fermentation promotion end temperature T2.
(15 degrees Celsius), heater controller 2
The power supply to the heater 14 is cut off via 1 and the operation returns to the normal operation.

【0019】なお、発酵促進のための予熱運転を自動的
に行わせるようにしたが、槽内温度(検出温度XT)
は、制御盤22の槽内温度表示部23により知ることが
できるので、制御盤22に発酵促進スイッチを配設し、
人為的に発酵促進のための予熱運転を行わせるようにし
ても良い。また、何れの場合も、この発酵促進のための
予熱運転時に切返し手段2を作動させるようにしても良
い。
The preheating operation for accelerating the fermentation is automatically performed. However, the temperature in the tank (detection temperature XT)
Can be known from the in-bath temperature display section 23 of the control panel 22, so that a fermentation promotion switch is provided on the control panel 22,
Preheating operation for artificially promoting fermentation may be performed. In any case, the switching means 2 may be operated during the preheating operation for promoting fermentation.

【0020】以上の運転中において、図4のフローチャ
ートに示す割り込み処理が行われる。即ち、運転中の生
ゴミの投入などのために投入口8の蓋7が開けられ、開
蓋センサー17がオンすると、モーターコントローラー
21を介して切返し手段2の駆動用モーター6に対する
通電が断たれ、処理槽1内のリボンスクリュー4,5の
回転が止められるとともに、モーターコントローラー2
0を介して通風手段11の送風機15が強制的に強風オ
ンに切り換えられる。この結果、回転するリボンスクリ
ュー4,5による人身事故を防止できるとともに、開い
た投入口8からも外気が強力に槽内に吸引されるので、
投入される生ゴミや槽内から塵埃や臭気が生ゴミ投入作
業者側に飛散するのを防止できる。投入口8の蓋7が閉
じられ、開蓋センサー17がオフになると、この割り込
み制御は終了し、元の定常運転に復帰する。
During the above operation, an interruption process shown in the flowchart of FIG. 4 is performed. That is, when the lid 7 of the input port 8 is opened for the input of garbage during operation or the like and the lid open sensor 17 is turned on, the power supply to the drive motor 6 of the switching means 2 via the motor controller 21 is cut off. The rotation of the ribbon screws 4 and 5 in the processing tank 1 is stopped, and the motor controller 2
0, the blower 15 of the ventilation means 11 is forcibly switched on. As a result, personal injury due to the rotating ribbon screws 4 and 5 can be prevented, and the outside air is also strongly sucked into the tank from the opened inlet 8.
It is possible to prevent dust or odor from being thrown into the garbage input worker side from the garbage to be input or from inside the tank. When the lid 7 of the charging port 8 is closed and the lid opening sensor 17 is turned off, the interruption control ends, and the operation returns to the original steady operation.

【0021】生ゴミ投入後、所定時間を経過しても生ゴ
ミの発酵分解が進まず、検出温度XTが上がらなくな
り、腐敗臭が生じるようになった場合、床材を入れ替え
る。この場合、運転スイッチ24をオフ操作して取り出
しスイッチ25をオン操作する。勿論、取り出しスイッ
チ25のオン操作により、運転スイッチ24が自動的に
オフになるように構成することもできる。図5のフロー
チャートに示すように、取り出しスイッチ25のオン操
作により、投入口8の蓋7が閉じられて開蓋センサー1
7がオフであることを条件に、モーターコントローラー
21を介して切返し手段2の駆動用モーター6に対し連
続通電され、処理槽1内のリボンスクリュー4,5が連
続回転する。この状態で取り出し口10の蓋9を開き、
この取り出し口10の方へ送り作用のある小径の右送り
用リボンスクリュー4により、処理槽1内の床材を取り
出し口10より排出させる。この取り出し運転中に投入
口8の蓋7が開かれて開蓋センサー17がオンすると、
リボンスクリュー4,5が停止する。
If the fermentation decomposition of the garbage does not proceed even after a predetermined time has elapsed after the garbage is put in, and the detected temperature XT does not rise and a putrid odor is generated, the floor material is replaced. In this case, the operation switch 24 is turned off and the take-out switch 25 is turned on. Of course, the operation switch 24 can be automatically turned off by turning on the take-out switch 25. As shown in the flowchart of FIG. 5, when the take-out switch 25 is turned on, the lid 7 of the slot 8 is closed and the lid-opening sensor 1 is closed.
On condition that the switch 7 is off, the drive motor 6 of the switching means 2 is continuously energized via the motor controller 21 and the ribbon screws 4 and 5 in the processing tank 1 rotate continuously. In this state, open the lid 9 of the outlet 10 and
The floor material in the processing tank 1 is discharged from the take-out port 10 by the small-diameter right-feed ribbon screw 4 having a feed action toward the take-out port 10. When the cover 7 of the inlet 8 is opened and the cover open sensor 17 is turned on during the removal operation,
The ribbon screws 4 and 5 stop.

【0022】なお、図1及び図2にそれぞれ仮想線で示
すように、処理槽1の底部から処理槽1内に外気を強制
送入する送気路27を併設することもできる。この底部
送気路27は、少なくとも排気路13と組み合わせて使
用されるが、底部送気路27と排気路13との内、少な
くとも何れか一方に送風機を併設すれば良い。28は送
気路27に組み込んだ送風機を示す。また、この送気路
27を設ける場合、ヒーター14はこの送気路27に組
み込むのが望ましい。送気路12は有っても無くとも良
い。
As shown by phantom lines in FIGS. 1 and 2, an air supply path 27 for forcibly supplying outside air from the bottom of the processing tank 1 into the processing tank 1 may be provided. The bottom air supply path 27 is used in combination with at least the exhaust path 13, and a blower may be provided in at least one of the bottom air supply path 27 and the exhaust path 13. Reference numeral 28 denotes a blower incorporated in the air passage 27. When the air supply path 27 is provided, it is desirable that the heater 14 be incorporated in the air supply path 27. The air supply path 12 may or may not be provided.

【0023】さらに、切返し手段2による切返し作用を
弱めた弱切返し制御として、間欠運転される切返し手段
2の駆動時間に対する停止時間の割合を大きくし、切返
し手段2による切返し作用を強めた強切返し制御とし
て、間欠運転される切返し手段2の駆動時間に対する停
止時間の割合を小さくしたが、弱切返し制御として、連
続駆動される切返し手段2の回転速度を低くし、強切返
し制御として、連続駆動される切返し手段2の回転速度
を高くすることもできる。また、間欠運転される切返し
手段2の駆動時間に対する停止時間の割合を変える場
合、一定駆動時間に対し停止時間の長さを変えたが、駆
動時間と停止時間の両方を変えても良いし、一定停止時
間に対し駆動時間の長さを変えても良い。
Further, as a weak switching control in which the switching action of the switching means 2 is weakened, the ratio of the stop time to the driving time of the switching means 2 which is operated intermittently is increased, and the strong switching control in which the switching action of the switching means 2 is enhanced. Although the ratio of the stop time to the drive time of the switching means 2 which is intermittently driven is reduced, the rotation speed of the continuously driven switching means 2 is reduced as the weak switching control, and the continuous driving is performed as the strong switching control. The rotation speed of the switching means 2 can be increased. Further, when changing the ratio of the stop time to the drive time of the switching means 2 that is operated intermittently, the length of the stop time is changed with respect to the constant drive time, but both the drive time and the stop time may be changed, The length of the drive time may be changed with respect to the fixed stop time.

【0024】[0024]

【発明の効果】以上のように本発明の生ゴミ処理方法に
よれば、処理槽内温度(温度センサーの検出温度)が、
摂氏35〜40度の範囲内で設定した設定発酵温度以下
のときは、材料切返し手段による切返し作用を弱めた弱
切返し制御と、通風手段の通風量を少なくした弱通風制
御との内、少なくとも何れか一方の制御を行い(実施形
態では両方であるが、何れか一方でも良い)、前記検出
温度が前記設定発酵温度以上のときは、材料切返し手段
による切返し作用を強めた強切返し制御と、通風手段の
通風量を大きくした強通風制御との内、少なくとも何れ
か一方の制御(実施形態では両方であるが、何れか一方
でも良い)を行うことにより、処理材料の発酵温度を摂
氏35〜40度の範囲内に抑えるのであるから、生ゴミ
の発酵分解の床として、発酵臭の吸着効果の高いバーク
などの木質系床材を使用することと相まって、発酵温度
が摂氏40度付近から急激に強くなる発酵臭を殆ど生ぜ
しめることなく、生ゴミの発酵分解を進行させ、生ゴミ
を消滅させることができる。
As described above, according to the garbage processing method of the present invention, the temperature in the processing tank (the temperature detected by the temperature sensor) is
When the fermentation temperature is equal to or lower than the set fermentation temperature set in the range of 35 to 40 degrees Celsius, at least one of the weak switching control in which the switching action of the material switching means is weakened and the weak ventilation control in which the ventilation amount of the ventilation means is reduced. When the detected temperature is equal to or higher than the set fermentation temperature, strong switching control in which the switching operation by the material switching means is enhanced and ventilation are performed. The fermentation temperature of the processing material is set to 35 to 40 degrees Celsius by performing at least one control (in the embodiment, both, or both may be used) of the strong ventilation control in which the ventilation amount of the means is increased. The fermentation temperature is around 40 degrees Celsius, in combination with the use of wood-based flooring such as bark, which has a high fermentation odor adsorption effect, as a bed for fermentation and decomposition of garbage. Et al rapidly almost without causing a made fermentation smell strongly, the fermentation decomposition of food waste is allowed to proceed, it is possible to eliminate the garbage.

【0025】従って、排気路に高価で保守の必要な消臭
装置を付加する必要がなく、設備コストの大幅な低減
と、作業環境の改善を図ることができる。しかも、前記
のように生ゴミの発酵分解の床として、それ自体も発酵
分解させることが可能なバークなどの木質系床材を使用
するのであるから、長期間の使用により、生ゴミの発酵
分解が効率良く行われなくなったとき、残った床材をそ
のまま堆肥として活用することも可能である。
Therefore, it is not necessary to add an expensive deodorizing device requiring maintenance to the exhaust path, so that the equipment cost can be greatly reduced and the working environment can be improved. In addition, as described above, a wooden flooring material such as bark, which itself can be fermented and decomposed, is used as a bed for fermentation and decomposition of garbage. When it is no longer efficiently performed, the remaining flooring can be used as it is as compost.

【0026】なお、請求項2に記載の本発明によれば、
適度の保湿性、通気性、柔軟性を持ち合わせたバーク堆
肥またはバーク堆肥を主成分とする床材を使用するの
で、新しい床材を使用した運転開始当初から効率良く生
ゴミの発酵分解を進行させることができるとともに、残
った床材を性状の良い良質の堆肥として再利用すること
ができる。
According to the second aspect of the present invention,
Since bark compost or a flooring material containing bark compost as a main component with appropriate moisture retention, air permeability and flexibility is used, the fermentation and decomposition of garbage can proceed efficiently from the beginning of operation using new flooring material. And the remaining flooring material can be reused as good-quality and high-quality compost.

【0027】また、請求項3に記載の本発明によれば、
切返し手段による切返しの強弱切り換えが容易且つ効果
的に行え、この切返しの強弱切り換えと通風の強弱切り
換えとの組み合わせにより、発酵温度を摂氏35〜40
度に効果的に抑えることができる。即ち、請求項1に記
載の本発明方法の実施が容易になる。
According to the third aspect of the present invention,
The switching of the switching by the switching means can be easily and effectively performed, and the combination of the switching of the switching and the switching of the ventilation allows the fermentation temperature to be 35 to 40 degrees Celsius.
Can be effectively suppressed each time. That is, the method according to the first aspect of the present invention can be easily performed.

【0028】また、請求項4に記載の本発明によれば、
寒冷地での使用や厳寒期での使用に際しても、生ゴミ投
入後の発酵を促進させ、効率良く所期の目的を達成し得
る。この場合、請求項5に記載の本発明によれば、ヒー
ターの作動開始温度を十分に低くしながら適度な温度ま
で槽内を加熱することができるので、ヒーター作動によ
るランニングコストの上昇を抑えることができる。さら
にこの場合、請求項6に記載の本発明によれば、処理槽
内を流通する空気を利用して処理槽内を容易にむらなく
加熱することができる。
According to the present invention described in claim 4,
Even when used in a cold region or in a severe cold season, fermentation after putting in garbage can be promoted, and the intended purpose can be achieved efficiently. In this case, according to the present invention, since the inside of the tank can be heated to an appropriate temperature while sufficiently lowering the operation start temperature of the heater, it is possible to suppress an increase in running cost due to the operation of the heater. Can be. Furthermore, in this case, according to the present invention, the inside of the processing tank can be easily and uniformly heated using the air flowing in the processing tank.

【0029】さらに、請求項7に記載の本発明によれ
ば、生ゴミの投入などのために処理槽の投入口が開かれ
たとき、処理槽内から塵埃や臭気が噴き上がるのを防止
することができ、作業環境がより一層改善される。ま
た、請求項8に記載の本発明によれば、槽内に送入され
た外気を切返し手段で切返し攪拌される処理材料中に効
率良く通気させて、発酵に伴う温度上昇を良好に抑制す
ることができる。
Further, according to the present invention, when the input port of the processing tank is opened for the input of raw garbage, dust and odor are prevented from spouting from inside the processing tank. And the working environment is further improved. According to the present invention as set forth in claim 8, the outside air fed into the tank is efficiently aerated into the processing material which is repeatedly stirred by the switching means, and the temperature rise accompanying fermentation is favorably suppressed. be able to.

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

【図1】 本発明方法の実施に使用できる処理装置の縦
断側面図と制御系の構成を説明するブロック線図であ
る。
FIG. 1 is a vertical sectional side view of a processing apparatus that can be used to carry out a method of the present invention, and a block diagram illustrating a configuration of a control system.

【図2】 前記処理装置の縦断正面図である。FIG. 2 is a vertical sectional front view of the processing apparatus.

【図3】 本発明方法の制御手順を説明するフローチャ
ートである。
FIG. 3 is a flowchart illustrating a control procedure of the method of the present invention.

【図4】 割り込み制御手順を説明するフローチャート
である。
FIG. 4 is a flowchart illustrating an interrupt control procedure.

【図5】 床材取り出し時の制御手順を説明するフロー
チャートである。
FIG. 5 is a flowchart illustrating a control procedure at the time of floor material removal.

【符号の説明】[Explanation of symbols]

1 処理槽 2 切返し手段 4 小径の右送り用リボンスクリュー 5 大径の左送り用リボンスクリュー 6 モーター 8 投入口 10 取り出し口 11 通風手段 12,27 送気路 13 排気路 14 ヒーター 15,28 送風機 16 温度センサー 17 開蓋センサー 18 制御装置 22 制御盤 23 槽内温度表示部 24 運転スイッチ 25 取り出しスイッチ REFERENCE SIGNS LIST 1 processing tank 2 switching means 4 small-diameter right-feed ribbon screw 5 large-diameter left-feed ribbon screw 6 motor 8 input port 10 take-out port 11 ventilation means 12, 27 air supply path 13 exhaust path 14 heater 15, 28 blower 16 Temperature sensor 17 Opening sensor 18 Controller 22 Control panel 23 Temperature display section inside tank 24 Operation switch 25 Extraction switch

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】処理槽と、当該処理槽内の材料切返し手段
と、槽内温度を検出する温度センサーと、槽内に外気を
通す通風手段とを備えた処理装置を使用し、処理槽内に
バークなどの木質系床材と生ゴミとを収容し、材料切返
し手段と通風手段を作動させて、生ゴミを処理する生ゴ
ミ処理方法であって、 前記温度センサーの検出温度が、摂氏35〜40度の範
囲内で設定した設定発酵温度以下のときは、材料切返し
手段による切返し作用を弱めた弱切返し制御と、通風手
段の通風量を少なくした弱通風制御との内、少なくとも
何れか一方の制御を行い、前記検出温度が前記設定発酵
温度以上のときは、材料切返し手段による切返し作用を
強めた強切返し制御と、通風手段の通風量を大きくした
強通風制御との内、少なくとも何れか一方の制御を行う
ことにより、処理材料の発酵温度を摂氏35〜40度の
範囲内に抑えることを特徴とする、生ゴミ処理方法。
1. A processing apparatus comprising a processing tank, a material switching means in the processing tank, a temperature sensor for detecting a temperature in the tank, and a ventilation means for passing outside air into the tank. A wood-based flooring material such as bark and garbage, and a garbage disposal method for treating garbage by operating the material switching means and the ventilation means, wherein the temperature detected by the temperature sensor is 35 degrees Celsius. When the temperature is equal to or lower than the set fermentation temperature set within the range of 4040 ° C., at least one of the weak switching control in which the switching action of the material switching means is weakened and the weak ventilation control in which the ventilation amount of the ventilation means is reduced. When the detected temperature is equal to or higher than the set fermentation temperature, at least one of strong switching control in which the switching operation by the material switching unit is strengthened and strong ventilation control in which the ventilation amount of the ventilation unit is increased. One of the controls A method for treating garbage, wherein the method controls the fermentation temperature of the treated material within a range of 35 to 40 degrees Celsius.
【請求項2】前記木質系床材が、バーク堆肥またはバー
ク堆肥を主成分とするものである、請求項1に記載の生
ゴミ処理方法。
2. The garbage disposal method according to claim 1, wherein said wood flooring is bark compost or bark compost as a main component.
【請求項3】前記検出温度が前記設定発酵温度以下のと
きは、間欠運転される材料切返し手段の駆動時間に対す
る停止時間の割合を大きくした弱切返し制御を行うとと
もに、通風手段の通風量を少なくした弱通風制御とを行
い、前記検出温度が前記設定発酵温度以上のときは、間
欠運転される材料切返し手段の駆動時間に対する停止時
間の割合を小さくした強切返し制御を行うとともに、通
風手段の通風量を大きくした強通風制御とを行うことを
特徴とする、請求項1または2に記載の生ゴミ処理方
法。
3. When the detected temperature is equal to or lower than the set fermentation temperature, weak return control is performed by increasing the ratio of the stop time to the drive time of the intermittently operated material switching means, and the ventilation amount of the ventilation means is reduced. When the detected temperature is equal to or higher than the set fermentation temperature, strong switching control is performed by reducing the ratio of the stop time to the driving time of the material switching means that is intermittently operated, and the ventilation of the ventilation means is performed. The garbage disposal method according to claim 1, wherein a strong ventilation control with an increased amount is performed.
【請求項4】槽内雰囲気温度を高めるヒーターを併設
し、外気温度または前記検出温度が、摂氏20度以下に
設定された発酵促進開始温度以下のときのみ、前記ヒー
ターを作動させることを特徴とする、請求項1〜3の何
れかに記載の生ゴミ処理方法。
4. A heater for increasing the atmosphere temperature in the tank is provided, and the heater is operated only when the outside air temperature or the detected temperature is equal to or lower than a fermentation acceleration start temperature set at 20 degrees Celsius or lower. The garbage disposal method according to any one of claims 1 to 3.
【請求項5】外気温度または前記検出温度が、摂氏10
度以下に設定された発酵促進開始温度以下のとき、前記
ヒーターを作動させ、外気温度または前記検出温度が、
摂氏10〜20度範囲内に設定された発酵促進終了温度
以上のとき、前記ヒーターを停止させることを特徴とす
る、請求項4に記載の生ゴミ処理方法。
5. The method according to claim 1, wherein the outside air temperature or said detected temperature is 10 degrees Celsius.
When the temperature is equal to or lower than the fermentation promotion start temperature set to be less than or equal to the degree, the heater is operated, and the outside air temperature or the detected temperature is
The garbage disposal method according to claim 4, wherein the heater is stopped when the temperature is equal to or higher than the fermentation promotion end temperature set within a range of 10 to 20 degrees Celsius.
【請求項6】前記ヒーターが前記通風手段の槽内への送
気路中に配設されている、請求項4または5に記載の生
ゴミ処理方法。
6. The garbage disposal method according to claim 4, wherein the heater is disposed in an air passage of the ventilation means into a tank.
【請求項7】前記通風手段が、槽内への送気路と、槽外
への排気路と、当該排気路中に配設された送風機とを有
し、処理槽の投入口が開かれている間、前記送風機の通
風を強に切り換えることを特徴とする、請求項1〜6の
何れかに記載の生ゴミ処理方法。
7. The ventilation means has an air supply path into the tank, an exhaust path to the outside of the tank, and a blower disposed in the exhaust path, and an inlet of the processing tank is opened. The garbage disposal method according to any one of claims 1 to 6, wherein the ventilation of the blower is strongly switched during the operation.
【請求項8】前記通風手段が、槽内底部に外気を送入す
る送気路を備えていることを特徴とする、請求項1〜7
の何れかに記載の生ゴミ処理方法。
8. The ventilation means according to claim 1, wherein said ventilation means is provided with an air supply passage for supplying outside air to a bottom of said tank.
A garbage disposal method according to any one of the above.
JP12516099A 1999-04-30 1999-04-30 Garbage disposal method Expired - Fee Related JP3504881B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12516099A JP3504881B2 (en) 1999-04-30 1999-04-30 Garbage disposal method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12516099A JP3504881B2 (en) 1999-04-30 1999-04-30 Garbage disposal method

Publications (2)

Publication Number Publication Date
JP2000317423A true JP2000317423A (en) 2000-11-21
JP3504881B2 JP3504881B2 (en) 2004-03-08

Family

ID=14903371

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Application Number Title Priority Date Filing Date
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Country Link
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002205034A (en) * 2001-01-11 2002-07-23 Matsushita Electric Works Ltd Machine for treating garbage
CN100389894C (en) * 2005-10-21 2008-05-28 北京师范大学 Automatic ventilating control and controller for waste uniform degradation by temperature gradient feedback
JP2012229136A (en) * 2011-04-26 2012-11-22 Obihiro Univ Of Agriculture & Veterinary Medicine Compost producing method and device

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002205034A (en) * 2001-01-11 2002-07-23 Matsushita Electric Works Ltd Machine for treating garbage
JP4560961B2 (en) * 2001-01-11 2010-10-13 パナソニック電工株式会社 Garbage processing machine
CN100389894C (en) * 2005-10-21 2008-05-28 北京师范大学 Automatic ventilating control and controller for waste uniform degradation by temperature gradient feedback
JP2012229136A (en) * 2011-04-26 2012-11-22 Obihiro Univ Of Agriculture & Veterinary Medicine Compost producing method and device

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