JPH10202230A - Garbage treating machine - Google Patents

Garbage treating machine

Info

Publication number
JPH10202230A
JPH10202230A JP9010913A JP1091397A JPH10202230A JP H10202230 A JPH10202230 A JP H10202230A JP 9010913 A JP9010913 A JP 9010913A JP 1091397 A JP1091397 A JP 1091397A JP H10202230 A JPH10202230 A JP H10202230A
Authority
JP
Japan
Prior art keywords
garbage
heater
temp
base material
time
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.)
Withdrawn
Application number
JP9010913A
Other languages
Japanese (ja)
Inventor
Takeshi Fukuchi
毅 福地
Kenichi Hamada
研一 浜田
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.)
Hitachi Ltd
Hitachi Appliances Techno Service Ltd
Original Assignee
Hitachi Ltd
Hitachi Taga Technology 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 Ltd, Hitachi Taga Technology Ltd filed Critical Hitachi Ltd
Priority to JP9010913A priority Critical patent/JPH10202230A/en
Publication of JPH10202230A publication Critical patent/JPH10202230A/en
Withdrawn legal-status Critical Current

Links

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To prolong the life of base materials and to prevent the generation of malodors by activating a heat insulating heater at the heat generating temp. higher than an environment temp. only in the period during the specific time from the time a user charges crude refuse into a treating vessel when the fermentation temp. of the base material is low and the moisture evaporation is little. SOLUTION: The temp. of the base materials 23, such as sawdust and chaff, rises gradually by spending 3 to 5 hours after charging of the crude refuse, attains the max. temp. in 6 to 9 hours and gradually falls again with the garbage treating machine which puts the base materials 23 and aerobic bacteria into the crude refuse treating vessel 3 having agitating vanes 4 and a ventilator 15 and executes the decomposition treatment of the crude refuse by the effect of the aerobic bacteria. The surface cord heater 6 of the treating vessel 3 is so controlled as to act at the heat generating temp. higher than the environment temp. by an outdoor temp. sensor 19 in the period during the time of 3 to 5 hours after the charging of the crude refuse when the fermentation temp. of the base materials 23 is low and the moisture evaporation is little in synchronization with the rhythm. As a result, the evaporation of the moisture is accelerated and the activation of the bacteria is expedited.

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、厨芥処理機に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a garbage processing machine.

【0002】[0002]

【従来の技術】好気性バクテリアを利用して厨芥(以
下、生ごみという)を分解処理し、減量する技術は、例
えば特開平4−4084 号公報に開示されている。
2. Description of the Related Art A technique for decomposing kitchen garbage (hereinafter referred to as garbage) by using aerobic bacteria to reduce the weight is disclosed in, for example, JP-A-4-4084.

【0003】この生ごみ処理機は、撹拌羽根と換気装置
とを有する処理槽内に基材(微生物着床剤)と好気性バ
クテリアとを入れ、ここに破砕機を通して破砕した生ご
みを投入し、基材と生ごみとを撹拌する構成となってい
る。
[0003] In this garbage disposal machine, a substrate (microorganism implantation agent) and aerobic bacteria are put into a treatment tank having a stirring blade and a ventilator, and crushed garbage is put into this through a crusher. In addition, the structure is such that the base material and the garbage are stirred.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、上記の
公知例を含め従来の好気性バクテリアを利用する生ごみ
処理機であっては、基材の水分率の調整は基材の吸水作
用と発酵熱による水分の蒸発作用に頼っていた。このた
め投入される生ごみが西瓜やメロンのように水分が多か
ったり、生ごみの投入量が多い等、基材の水分調整能力
をオーバーした水分量が持ち込まれると、基材の水分率
が急増しジクジクした湿潤状態となり、好気性菌に必要
な通気が悪くなるので嫌気性菌の働きが強くなり、臭い
がでたり、処理能力が落ちて未処理残渣が多くなり、基
材の交換を要する「基材の寿命」に早く至ってしまう欠
点があった。
However, in the conventional garbage disposers utilizing the aerobic bacteria, including the above-mentioned known examples, the adjustment of the moisture content of the substrate depends on the water absorption of the substrate and the fermentation heat. Relied on the evaporation effect of water. For this reason, if the amount of raw garbage that is thrown in exceeds the moisture adjustment capacity of the base material, such as watermelon or watermelon that has a large amount of water, such as watermelon or melon, the moisture percentage of the base material will decrease. The aerobic bacteria required for aerobic bacteria are poorly ventilated due to a sudden increase in humid conditions, and the function of anaerobic bacteria becomes stronger. There is a disadvantage that the required "life of the base material" is quickly reached.

【0005】また正常な生ごみ処理状態でも、分解処理
を続けていくと、基材は撹拌により摩耗されて次第に微
細化かつ粒形も丸くなって粒子間の空隙が減少する。そ
の上、微小な生ごみの分解生成物が上記空隙に詰まって
くるので、基材内の空隙量従って空気量が大幅に減少し
通気も悪くなる。そのため好気性バクテリアの繁殖に不
適な環境状態となり発酵活動が低下し基材の温度が上が
らなくなるため内部の水分の蒸発が悪くなる。一方基材
の吸水も平衡吸水率に達するため、基材の水分率が増大
してベトベト,ジクジクした湿潤状態化し、固まりがで
きてくる。従って嫌気性バクテリアの働きが強くなり、
腐敗臭が出てくるとともに、生ごみの未処理残渣が多く
なり不快な状態となり実用上使用不能となる。
[0005] Even in a normal garbage treatment state, if the decomposition treatment is continued, the base material is worn by stirring and gradually becomes finer and the grain shape becomes rounder, so that voids between the particles are reduced. In addition, the decomposition products of minute garbage are clogged in the above-mentioned voids, so that the amount of voids in the base material, that is, the amount of air is greatly reduced, and the ventilation is also poor. Therefore, the environment becomes unsuitable for propagation of aerobic bacteria, fermentation activity is reduced, and the temperature of the base material does not rise. On the other hand, since the water absorption of the base material also reaches the equilibrium water absorption, the water content of the base material is increased, and the base material becomes sticky and humid, and forms a lump. Therefore, the action of anaerobic bacteria becomes stronger,
A rotten smell appears, and untreated residues of garbage increase, resulting in an unpleasant state, making it unusable practically.

【0006】また、基材の水分率が増大しベトベト,ジ
クジクした湿潤状態化すると、これを撹拌する撹拌羽根
の回転トルクが非常に大きくなる。このため、撹拌不能
となりロックしたり、撹拌羽根を駆動するモータと伝達
系とに無理がかかり、比較的早期のうちに故障する頻度
が高くなる。
In addition, when the moisture content of the base material increases and the base material becomes wet and greasy, the rotational torque of the stirring blade for stirring the base material becomes extremely large. For this reason, stirring becomes impossible, locking occurs, and the motor for driving the stirring blades and the transmission system are forced, and the frequency of failures increases relatively early.

【0007】そのため、使用不能になった古い基材を取
りだして、新しい基材と交換する作業が必要となる。こ
の基材が実用上使用不能となる「基材の寿命」が、短い
期間であると、基材交換作業は厄介で手間がかかる作業
であり、交換用の新しい基材にコストがかかることから
も好ましくない。
For this reason, it is necessary to take out the unusable old base material and replace it with a new base material. If the "substrate life" when the substrate becomes practically unusable is short, the replacement of the substrate is troublesome and time-consuming, and the cost of a new substrate for replacement is high. Is also not preferred.

【0008】この対策として従来は、基材そのものの量
を多くして、水分調整能力のアップを図る手段が取られ
てきた。そのため毎日連続しても処理できる生ごみの量
を表す「定格処理容量」1kgに対して必要な「基材容
積」は25リットルにもなり、機器の小形コンパクト化
とコスト低減を阻害する大きな要因となっていた。
As a countermeasure against this, conventionally, measures have been taken to increase the amount of the base material itself to increase the water adjusting ability. As a result, the required "base material volume" for 1 kg of "rated processing capacity", which indicates the amount of garbage that can be processed even every day, is as much as 25 liters, which is a major factor that hinders downsizing and cost reduction of equipment. Had become.

【0009】また、もう一つの対策として、保温ヒータ
による基材の加熱で水分蒸発を促進する法も取られてい
るが、バクテリアの活動から生じる基材の温度サイクル
に関係なく長時間加熱するため、電力消費が大きくラン
ニングコストがかかる上に、発酵熱が高い時と重なり、
基材温度が高くなり過ぎ、臭いがでる等の欠点があっ
た。
As another countermeasure, a method of promoting water evaporation by heating the base material with a warming heater has been adopted. However, since the base material is heated for a long time regardless of the temperature cycle of the base material caused by the activity of bacteria. , Power consumption is large, running costs are high, and the fermentation heat is high,
There were drawbacks such as the base material temperature becoming too high and odor coming out.

【0010】本発明の目的は上記課題を解決し、基材の
長寿命を図るとともに悪臭の発生を防止した厨芥処理機
を提供することにある。
An object of the present invention is to solve the above-mentioned problems and to provide a garbage disposer capable of prolonging the life of a base material and preventing generation of offensive odor.

【0011】[0011]

【課題を解決するための手段】上記目的は、撹拌羽根と
換気装置とを有する生ごみ処理槽内に基材と好気性バク
テリアとを入れ、生ごみを投入し、基材と生ごみとを撹
拌する生ごみ処理機において、上記生ごみ処理槽の外周
面に面状ヒータを貼り付けた構成の保温ヒータと機器の
環境温度を測定する外気温度センサとを設け、処理槽に
使用者が生ごみを投入した時から3〜5時間の間の、基
材の発酵温度が低く水分蒸発が少ない期間のみ、環境温
度より高い発熱温度で保温ヒータを働かせて、水分の蒸
発促進を計ることにより達成することができる。
The object of the present invention is to put a base material and aerobic bacteria into a garbage processing tank having a stirring blade and a ventilation device, throw in garbage, and separate the base material and the garbage. In the garbage processing machine to be agitated, a warming heater having a configuration in which a planar heater is attached to the outer peripheral surface of the garbage processing tank and an outside air temperature sensor for measuring the environmental temperature of the equipment are provided. Achieved by operating the heat retention heater at an exothermic temperature higher than the environmental temperature only during the period when the fermentation temperature of the base material is low and water evaporation is small during the period of 3 to 5 hours after the garbage is thrown, thereby promoting the evaporation of water. can do.

【0012】処理槽内の基材の温度は、バクテリアの生
活リズムによって変化する。生ごみの種類や環境温度に
より多少異なるが、活動のエネルギ源となる栄養源
(餌)即ち生ごみが与えられてた時を起点として、極め
てゆっくりと3〜5時間かけて徐々に温度を上げてい
き、3〜5時間目より急峻に温度を上昇して、6〜9時
間目で最高温度に達し、再び極めて徐々に温度をさげて
いく。このリズムに合わせて、使用者が生ごみを投入し
た時から3〜5時間の間の、基材の発酵温度が低く水分
蒸発が少ない期間のみ、処理槽の外周面に面状ヒータを
貼り付けた構成の保温ヒータを、環境温度を測定する外
気温度センサにより制御して、環境温度より高い発熱温
度で働かせて、水分の蒸発促進を計るとともに、バクテ
リアの活性化を早めてやることにより達成することがで
きる。
[0012] The temperature of the substrate in the treatment tank changes according to the life rhythm of bacteria. Depending on the type of garbage and the environmental temperature, the temperature gradually increases over a period of 3 to 5 hours very slowly starting from the nutrient source (feed) that is the energy source of the activity, that is, when the garbage is given. Then, the temperature rises sharply from the third to fifth hours, reaches the maximum temperature in the sixth to ninth hours, and gradually decreases again. According to this rhythm, a sheet heater is attached to the outer peripheral surface of the treatment tank only during the period when the fermentation temperature of the base material is low and the water evaporation is small during 3 to 5 hours from the time when the user puts the garbage. Achieved by controlling the heat retention heater with the external air temperature sensor that measures the environmental temperature and operating at a heat generation temperature higher than the environmental temperature to promote the evaporation of moisture and accelerate the activation of bacteria. be able to.

【0013】[0013]

【発明の実施の形態】以下、本発明の実施の形態の一例
を、図面を用いて説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the drawings.

【0014】図1は本発明の実施形態に係る生ごみ厨芥
処理装置の全体構成を示す斜視図、図2は図1の縦断面
図、図3は図2のA−A線断面図、図4は面状コードヒ
ータの構成を断面して示す斜視図である。
FIG. 1 is a perspective view showing an entire configuration of a kitchen garbage disposal apparatus according to an embodiment of the present invention, FIG. 2 is a longitudinal sectional view of FIG. 1, and FIG. 3 is a sectional view taken along line AA of FIG. FIG. 4 is a perspective view showing a cross section of the configuration of the planar cord heater.

【0015】図1ないし図2において、生ごみ処理装置
1は、内部に生ごみ処理槽3を配置された筐体2と、生
ごみ処理槽3の中央部で水平方向に取り付けられた回転
軸5に設けられた撹拌羽根4と、生ごみ処理槽3の外周
部に貼付された面状コードヒータ6と、この面状コード
ヒータ6の発熱温度を決める環境温度を測定する外気温
度センサ29、及びこれらの動作を制御する制御装置7
とから基本的に構成されている。
In FIG. 1 and FIG. 2, a garbage processing apparatus 1 includes a housing 2 in which a garbage processing tank 3 is disposed, and a rotating shaft horizontally mounted at the center of the garbage processing tank 3. 5, an agitating blade 4 provided in the garbage processing unit 5, a planar cord heater 6 attached to an outer peripheral portion of the garbage disposal tank 3, an outside air temperature sensor 29 for measuring an environmental temperature for determining a heating temperature of the planar cord heater 6, And a control device 7 for controlling these operations
It is basically composed of

【0016】生ごみ処理槽3は、扁平な円筒形状に形成
され、その中央部に前記回転軸5が一対の軸受8に支持
されている。回転軸5の一端は図3に示すように生ごみ
処理槽3から突出し、その突出部分に従動側のプーリ9
が回転軸5と一体に回転するように軸着され、回転軸5
の生ごみ処理槽3内に位置する部分には、3枚の撹拌羽
根4が円周方向に等角度で、軸方向に等間隔に立設され
ている。
The garbage disposal tank 3 is formed in a flat cylindrical shape, and the rotating shaft 5 is supported by a pair of bearings 8 at the center thereof. One end of the rotating shaft 5 protrudes from the garbage disposal tank 3 as shown in FIG.
Are mounted so as to rotate integrally with the rotating shaft 5, and the rotating shaft 5
In the portion located in the garbage processing tank 3, three stirring blades 4 are provided upright at equal angles in the circumferential direction and at equal intervals in the axial direction.

【0017】前記従動側プーリ9と筐体2の底部に固定
されたモータ10の回転軸に軸着された駆動側のプーリ
11との間にはベルト12が掛け渡され、モータ10の
動力を回転軸5に伝達できるようになっている。なおプ
ーリ9,10とベルト40に代えてスプロケットとチェ
ーンを使用することもできる。
A belt 12 is stretched between the driven pulley 9 and a driving pulley 11 which is mounted on a rotating shaft of a motor 10 fixed to the bottom of the housing 2, so that the power of the motor 10 is supplied. The power can be transmitted to the rotating shaft 5. Note that sprockets and chains can be used instead of the pulleys 9 and 10 and the belt 40.

【0018】筐体2の上部の両側には図2に示すように
フィルタ13a,14aを備えた吸気口13と排気口1
4とが設けられ、排気口14には換気用のファン15が
設置されている。このファン15は図示しないモータに
よって駆動され、新鮮な空気を吸気口13から処理槽3
内に導入し、排気口14から処理槽3内のガス、例えば
炭酸ガスや発酵に伴う臭いを含んだガス等を筐体2の外
に排出する。
On both sides of the upper part of the housing 2, as shown in FIG. 2, an intake port 13 having filters 13 a and 14 a and an exhaust port 1 are provided.
4 are provided, and a ventilation fan 15 is provided at the exhaust port 14. The fan 15 is driven by a motor (not shown) to supply fresh air from the intake port 13 to the processing tank 3.
The gas in the processing tank 3, for example, a gas containing carbon dioxide gas or a odor accompanying fermentation, is discharged from the housing 2 through the exhaust port 14.

【0019】また筐体2の上端面には処理槽3の上部に
連通する生ごみ投入口16が開設され、内蓋17と外蓋
18とによって、前記投入口16は二重に施蓋される。
なお、蓋の密閉度を確保するために内蓋17と外蓋18
には、それぞれの受け面との間をシールするパッキンが
設けられている。また投入口16の裏面に当たる部分に
は各種の動作制御を行う制御装置7が設けられている。
A food waste inlet 16 communicating with the upper part of the processing tank 3 is opened at the upper end surface of the housing 2, and the inlet 16 is double-covered by an inner lid 17 and an outer lid 18. You.
Note that the inner lid 17 and the outer lid 18 are used to secure the tightness of the lid.
Are provided with packings for sealing between respective receiving surfaces. Further, a control device 7 for performing various operation controls is provided in a portion corresponding to the back surface of the insertion port 16.

【0020】処理槽3の底部には、内容物を取り出すた
めの排出口19が設けられている。排出口19は、通
常、取っ手20を有する引出式のシャッター21で遮蔽
されており、取っ手20に手を掛けてシャッター21を
引き出すと、処理槽3の内容物は排出口19から排出路
22に落ち込むので、これを掻きだすことにより筐体2
から外に取りだすことができる。
At the bottom of the processing tank 3, an outlet 19 for taking out the contents is provided. The discharge port 19 is normally shielded by a pull-out type shutter 21 having a handle 20. When the user puts his hand on the handle 20 and pulls out the shutter 21, the contents of the processing tank 3 are discharged from the discharge port 19 to the discharge path 22. Since it falls down, it is
Can be taken out of the

【0021】生ごみ処理槽3の内部には、基材23が入
っている。基材23はリグニン,セルローズ,ヘミセル
ローズ等の生分解性の悪いものを主成分とするもので、
具体的には、おがくず,もみがらや稲のわらを裁断した
もの等で、その一粒一粒が多孔質で空隙を有し、かつ粒
形が複雑で、でこぼこしていて、粒と粒との間に大きな
空隙が形成されているようなものである。
A substrate 23 is contained in the garbage disposal tank 3. The base material 23 is mainly composed of a material having poor biodegradability such as lignin, cellulose, hemicellulose, etc.
Concretely, sawdust, rice husk, rice straw, etc. are cut, and each grain is porous and has voids, and the grain shape is complicated, uneven, and It is as if a large gap is formed between them.

【0022】外蓋18には、ドアスイッチ77(図示せ
ず)が連動しており、外蓋18を所定の角度まで開ける
と、ドアスイッチが開放されて、制御装置7がこれに従
って回転軸5の電源を切ることによって、撹拌羽根4が
止まるよう構成されている。処理槽3は洗濯機の洗濯槽
などに広く使われているポリプロピレン樹脂(以下PP
樹脂という)で成形し、その外周面には広い面積に渡っ
て面状コードヒータ6が接着され、さらに面状コードヒ
ータ6を断熱発泡体シート24,24aによってカバー
している。面状コードヒータ6は図4に示すように細い
コイル状に巻かれた発熱線25を、テトロンのコード2
6を芯としてその外周に螺旋状に巻き付け、その上を絶
縁皮膜27でコーティングしコード状にしたものを、ア
ルミニウムのシート28の上に這わせるようにして接着
したものである。図示しないサーミスタにより発熱温度
を監視し温度制御機構により、その発熱温度を所定の設
定値に保つことができるようになっている。
A door switch 77 (not shown) is interlocked with the outer lid 18. When the outer lid 18 is opened to a predetermined angle, the door switch is opened, and the controller 7 operates the rotary shaft 5 in accordance with the door switch. The stirring blade 4 is configured to be stopped by turning off the power supply. The processing tub 3 is made of a polypropylene resin (hereinafter referred to as PP) widely used in a washing tub of a washing machine.
The sheet cord heater 6 is adhered to the outer peripheral surface over a wide area, and the sheet cord heater 6 is further covered with heat insulating foam sheets 24 and 24a. As shown in FIG. 4, the planar cord heater 6 applies a heating wire 25 wound in a thin coil shape to the cord 2 of Tetron.
6 is helically wound around its outer periphery, coated with an insulating film 27 and formed into a cord, and adhered so as to be laid on an aluminum sheet 28. The heating temperature is monitored by a thermistor (not shown), and the heating temperature can be kept at a predetermined set value by a temperature control mechanism.

【0023】処理槽3内には熱伝導の悪いおがくず等か
らなる前記基材23が入っているが、この面状コードヒ
ータ6を広い面積に渡って貼り付けることにより均一に
加熱することができるようになっている。29は機器の
環境温度を計るための外気温度センサである。
The processing tank 3 contains the base material 23 made of sawdust or the like having poor heat conductivity, but can be uniformly heated by sticking the planar cord heater 6 over a wide area. It has become. Reference numeral 29 denotes an outside air temperature sensor for measuring the environmental temperature of the device.

【0024】これらの面状コードヒータ6,外気温度セ
ンサ29,ドアスイッチ77及び回転軸5,換気ファン
10の駆動用モータ等の電気部品は、後述のように前記
制御装置7内のマイコンによりそのオン,オフの動作タ
イミングや動作の継続時間などが制御される。
The electric components such as the sheet code heater 6, the outside air temperature sensor 29, the door switch 77, the rotating shaft 5, and the motor for driving the ventilation fan 10 are controlled by a microcomputer in the control device 7 as described later. The ON / OFF operation timing and the operation continuation time are controlled.

【0025】以上のように構成した生ごみ処理装置1に
おいて、処理槽3内の基材23の水分率を40〜50%
に調節し、好気性バクテリアを投入して撹拌し、好気性
バクテリアが繁殖するための温床をつくる。あとは毎日
蓋を開閉して処理槽3内に生ごみを投入するだけで良
い。処理槽3内は、制御装置7によって所定の時間毎に
自動的に撹拌と換気とを交互に繰り返される。
In the garbage processing apparatus 1 configured as described above, the moisture content of the substrate 23 in the processing tank 3 is set to 40 to 50%.
The aerobic bacteria are charged and agitated to create a hotbed for aerobic bacteria to propagate. After that, it is only necessary to open and close the lid every day and throw garbage into the processing tank 3. In the processing tank 3, stirring and ventilation are automatically and alternately repeated at predetermined time intervals by the control device 7.

【0026】これにより、生ごみは基材23と共に撹拌
されることにより砕かれ、ギザギザな基材23の粒に擦
られて摩耗し、その表面に好気性バクテリアが付着し、
好気性バクテリアは生ごみを餌として食べ、繁殖する。
As a result, the garbage is crushed by being stirred with the substrate 23, and is rubbed and worn by the jagged particles of the substrate 23, and aerobic bacteria adhere to the surface thereof,
Aerobic bacteria feed on garbage and reproduce.

【0027】そして、生ごみはバラバラに発酵分解され
て、大部分は水蒸気と炭酸ガスとなり発散される。また
固形物として植物の養分となる低分子量化された分解生
成物即ち堆肥が生ごみ処理槽3の中に残される。発生ガ
スの中には微量ではあるが悪臭の原因となるアンモニ
ア,トリメチルアミン等のガスも含まれる。これらの水
蒸気や炭酸ガスその他のガス類は、換気の段階で前記フ
ァン15によって処理槽3から装置外に放出される。こ
の動作が断続的に自動運転により続けられる。
The garbage is fermented and decomposed into pieces, and most of the garbage is emitted as steam and carbon dioxide. In addition, low-molecular-weight decomposition products that become plant nutrients, that is, compost as solids, are left in the garbage disposal tank 3. The generated gas includes a small amount of gas such as ammonia and trimethylamine which causes a bad smell. These water vapor, carbon dioxide gas and other gases are discharged from the processing tank 3 to the outside of the apparatus by the fan 15 at the stage of ventilation. This operation is intermittently continued by automatic operation.

【0028】このような生ごみの処理動作が、使用条件
により時間の長短はあるが、2ヵ月から6ヵ月続くと、
基材23の摩耗と微粉化,吸水膨潤,生ごみの分解生成
物の蓄積、等が原因となり、空隙率の低下,通気性の悪
化と水分率の増大とから、好気性バクテリアの繁殖に不
適となり、発酵分解活動が低調化し、基材の温度が低下
して水分蒸発が悪くなる。そして基材23が粘性を帯
び、ベトベト,ジクジクした湿潤状態となり、ぼろぼろ
した固まりが発生してくる。この様な状態になると、基
材23内は次第に嫌気性バクテリアの働きが強くなって
きて、腐敗臭が出てくると共に、未分解の生ごみ残渣が
多くなり、不快感が増大して実用的に使用不能となる。
これが基材の寿命で、新しい基材23と交換する必要が
ある。この基材23の交換作業は厄介で手間がかかるこ
とと、新しく交換する基材23のコストがかかることか
ら、できるだけ基材の寿命を長くすることが重要な技術
課題となっている。
Although the processing of such garbage may take some time depending on the conditions of use, if it lasts 2 to 6 months,
It is unsuitable for propagation of aerobic bacteria due to a decrease in porosity, a decrease in air permeability and an increase in moisture content due to abrasion and pulverization of the base material 23, water absorption swelling, accumulation of decomposition products of garbage, and the like. And the fermentation decomposition activity is slowed down, the temperature of the base material is lowered, and the evaporation of water becomes worse. Then, the base material 23 becomes viscous, becomes sticky and jigged and wet, and a ragged mass is generated. In such a state, the action of the anaerobic bacteria gradually becomes stronger in the base material 23, and putrefaction odors are generated, and undecomposed garbage residues are increased. Becomes unusable.
This is the life of the substrate, and needs to be replaced with a new substrate 23. Since the replacement of the base material 23 is troublesome and time-consuming, and the cost of the replacement base material 23 is high, it is an important technical issue to extend the life of the base material as much as possible.

【0029】この対策として従来は、基材の量を多くし
て、水分調整能力のアップを図る手段が取られてきた。
このため生ごみ処理槽3が大きくなり、機器の小形コン
パクト化とコスト低減を阻害する大きな要因となってい
た。
As a countermeasure against this, conventionally, measures have been taken to increase the amount of the base material so as to increase the water adjusting ability.
For this reason, the garbage disposal tank 3 becomes large, which is a major factor that hinders downsizing and cost reduction of equipment.

【0030】もう一つの対策として、保温ヒータにより
基材を加熱し水分蒸発を促進する法もあるが、保温ヒー
タを長時間作動するため、電力消費が大きくランニング
コストがかかる上に、発酵温度が高い時と重なると基材
温度が高くなり過ぎ臭いがでる場合があるので、基材温
度測定センサ等による基材温度を監視しながら保温ヒー
タを自動運転する必要があり、コスト低減を阻害する等
の欠点があった。
As another countermeasure, there is a method of heating the base material with a warming heater to promote moisture evaporation. However, since the warming heater is operated for a long time, power consumption is large, running costs are increased, and the fermentation temperature is reduced. If the temperature is high, the temperature of the base material may become too high and smell may occur.Therefore, it is necessary to automatically operate the heat retention heater while monitoring the base material temperature using a base material temperature measurement sensor or the like, which hinders cost reduction. There were drawbacks.

【0031】これに対して、本発明においては、上記の
基材の寿命を長くする課題を、生ごみ処理槽3の外周面
に面状ヒータを貼り付けた構成の面状コードヒータ6
と、機器の環境温度を測定する外気温度センサ29とを
設け、処理槽3内の基材23の温度が、バクテリアの生
活リズムによって変化することに着目し、これを乱さず
に、基材温度が低い間だけ補助的に、外気温度より高く
なるように面状コードヒータ6を作動させることにより
解決している。
On the other hand, in the present invention, the problem of prolonging the life of the base material is solved by a planar cord heater 6 having a configuration in which a planar heater is attached to the outer peripheral surface of the garbage disposal tank 3.
And an outside air temperature sensor 29 for measuring the environmental temperature of the equipment, and paying attention to the fact that the temperature of the base material 23 in the processing tank 3 changes according to the rhythm of bacteria, without disturbing this. The problem is solved by operating the planar cord heater 6 so as to be higher than the outside air temperature only while the temperature is low.

【0032】即ち、基材23の温度は、生ごみの種類や
環境温度により多少異なるが、バクテリアの活動のエネ
ルギ源となる栄養源即ち生ごみが与えられてた時を起点
として、極めてゆっくりと3〜5時間かけて徐々に温度
を上げていき、3〜5時間目より急峻に温度を上昇し
て、6〜9時間目で最高温度に達し、再び極めて徐々に
温度をさげていく。このリズムに合わせて、使用者が生
ごみを投入した時から3〜5時間の間の、基材の発酵温
度が低く水分蒸発が少ない期間を狙って、処理槽3の面
状コードヒータ6を、外気温度センサ19による環境温
度を基準として、環境温度より高い発熱温度で働かせ
て、水分の蒸発促進を計るとともに、バクテリアの活性
化を早めるよう構成する。
That is, the temperature of the base material 23 is slightly different depending on the kind of garbage and the environmental temperature, but very slowly starting from a nutrient source serving as an energy source of bacterial activity, that is, garbage. The temperature is gradually increased over 3 to 5 hours, the temperature is sharply increased from the 3rd to 5th hours, reaches the maximum temperature in 6 to 9 hours, and is gradually decreased again. In accordance with this rhythm, the surface code heater 6 of the processing tank 3 is set for a period of 3 to 5 hours from the time when the user puts the garbage, in a period where the fermentation temperature of the base material is low and the water evaporation is small. By operating at an exothermic temperature higher than the ambient temperature based on the ambient temperature detected by the outside air temperature sensor 19, the evaporation of water is promoted and the activation of bacteria is accelerated.

【0033】これにより従来の基材量の半分位の基材量
で、基材の寿命を従来より長くすることができる。しか
も面状コードヒータ6の作動時間が短いので電力消費は
少なく、かつ面状コードヒータ6の動作制御が制御装置
7のマイコンによる時間制御で済むので極めて単純でコ
ストがかからない。これにより生ごみ処理機の大幅な小
形コンパクト化と低コスト化が達成される。
Thus, the life of the base material can be made longer than before with the base material amount which is about half of the conventional base material amount. In addition, since the operation time of the sheet code heater 6 is short, power consumption is small, and the operation control of the sheet code heater 6 can be performed by time control by the microcomputer of the control device 7, so that it is extremely simple and cost-effective. As a result, a significant reduction in size and cost of the garbage disposer is achieved.

【0034】ここで、処理槽3の面状コードヒータ6の
動作開始のタイミングである、使用者が生ごみを投入し
たことを知る手段として、生ごみを投入する時必ず外蓋
18が開閉されることに着目して、外蓋18に連動して
オン,オフするドアスイッチ77の開閉動作をもって判
断するようにすると、コストのかかる特別なセンサ類を
使用する必要がなく効果的である。
Here, as a means of knowing that the user has put in the garbage, which is the timing of starting the operation of the planar code heater 6 in the processing tank 3, the outer lid 18 is always opened and closed when the garbage is put in. By paying attention to this fact, it is effective to use the opening / closing operation of the door switch 77 which is turned on / off in conjunction with the outer lid 18 without using a special sensor which is expensive.

【0035】使用者が生ごみを投入した時から3〜5時
間の間のみ、面状コードヒータ6を動作するという単純
な制御では、使用者が生ごみの投入後内部の観察のため
何回も蓋を開閉したり、子供が遊びで蓋を開閉した場
合、面状コードヒータ6の動作時間が長くなって無駄な
電力消費になる恐れがあるが、一旦面状コードヒータ6
が動作を開始した初期の間は、外蓋18の開閉動作があ
っても無視し、面状コードヒータ6の動作時間の延長に
つながる動作指示を行わないようにすることにより防止
できる。または、一旦保温ヒータが動作した後は、所定
の動作時間が終了するまで、外蓋18の開閉動作があっ
ても、保温ヒータの動作時間の延長につながる動作指示
を行わないようにすることによっても防止することがで
きる。この様にすると制御装置7のマイコンのソフトが
簡単になる効果もある。
In the simple control of operating the sheet code heater 6 only for 3 to 5 hours from the time when the user puts the garbage, the user is required to observe the inside of the garbage several times after putting the garbage. When the lid is opened and closed, or when the child opens and closes the lid for play, the operation time of the planar cord heater 6 may be lengthened and wasteful power consumption may occur.
During the initial period of the start of the operation, the operation of opening and closing the outer lid 18 is ignored, and the operation instruction that extends the operation time of the planar code heater 6 can be prevented from being issued. Alternatively, after the heater is once operated, even if the opening / closing operation of the outer cover 18 is performed until the predetermined operating time is completed, an operation instruction that extends the operating time of the heater is prevented from being issued. Can also be prevented. This also has the effect of simplifying the software of the microcomputer of the control device 7.

【0036】また使用者が生ごみを投入した時から3〜
5時間の間のみ、面状コードヒータ6を動作するという
単純な制御では、使用者が生ごみの投入後、面状コード
ヒータ6が作動し所定の時間がきて作動停止したすぐ後
で、次の生ごみの投入をされると、再び面状コードヒー
タ6が作動することになる。結局一日の大半面状コード
ヒータ6が動作してしまったということでは、電力消費
が非常に大きくなってしまう。この欠点は面状コードヒ
ータ6の一日当たりの総動作時間を制限することにより
解決される。
In addition, three to three hours after the user throws in the garbage
In the simple control in which the sheet code heater 6 is operated only for 5 hours, after the user inputs the garbage, immediately after the sheet code heater 6 is operated and the operation is stopped after a predetermined time, the next time. When the garbage is supplied, the planar cord heater 6 is operated again. After all, the fact that most of the planar cord heaters 6 have been operated for a day means that the power consumption is extremely large. This drawback is solved by limiting the total operating time per day of the sheet code heater 6.

【0037】例えば一日、24時間内に8時間以上は動
作しないようにする。もしくは一日当たりの面状コード
ヒータ6の動作回数を制限することによっても解決され
る。例えば一日24時間内の面状コードヒータ6の動作
回数を3回以下とする。この一日の面状コードヒータの
動作回数を制限する手段として、面状コードヒータ6が
所定時間の動作を終了した後の一定の時間の間、外蓋1
8の開閉動作があっても、面状コードヒータ6を作動さ
せないようにすると、制御装置7のマイコンのソフトが
簡単ですむ効果を有する。
For example, no operation is performed for more than 8 hours within 24 hours a day. Alternatively, the problem can be solved by limiting the number of operations of the planar cord heater 6 per day. For example, the number of operations of the planar code heater 6 within 24 hours a day is set to three or less. As means for limiting the number of times of operation of the sheet code heater in one day, the outer lid 1 is kept for a certain time after the sheet code heater 6 has completed the operation for a predetermined time.
If the planar code heater 6 is not operated even when the opening / closing operation of the control unit 8 is performed, the software of the microcomputer of the control device 7 can be simplified.

【0038】[0038]

【発明の効果】本発明によれば、おがくず等の基材を利
用した生ごみ処理機において、基材の水分調整を従来の
ように、基材そのものの吸水力と発酵熱による水分蒸発
にのみ頼らずに、処理槽の外周面に保温ヒータを設け、
生ごみ投入後の3〜5時間の間の発酵熱の低い時間の
み、保温ヒータを、外気温度センサによる外気温度をべ
ースに、外気温度より高い発熱温度で働かせ、水分蒸発
の不足分を補完してやることによって、極めて少ない電
力消費で、基材量を従来よりも大幅に少なくしても十分
な処理性能と基材寿命を得ることができる。これにより
機器の大幅な小形コンパクト化と低コスト化ができる。
According to the present invention, in a garbage disposer using a substrate such as sawdust and the like, the water content of the substrate is adjusted only by the water absorption power of the substrate itself and the water evaporation by the heat of fermentation as in the prior art. Without relying on it, install a heat retention heater on the outer peripheral surface of the processing tank,
Only during the period of low fermentation heat between 3 and 5 hours after the input of garbage, the heat retention heater is operated at a temperature higher than the outside air temperature based on the outside air temperature by the outside air temperature sensor, and the shortage of water evaporation is reduced. By supplementing them, it is possible to obtain a sufficient processing performance and a long life of the substrate with extremely low power consumption even if the amount of the substrate is significantly reduced as compared with the conventional case. As a result, the size and size of the device can be significantly reduced, and the cost can be reduced.

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

【図1】本発明の一実施例である厨芥処理機の全体構成
を示す斜視図である。
FIG. 1 is a perspective view showing the overall configuration of a kitchen waste treatment machine according to one embodiment of the present invention.

【図2】図1の縦断側面図である。FIG. 2 is a vertical sectional side view of FIG.

【図3】図2のA−A断面図である。FIG. 3 is a sectional view taken along line AA of FIG. 2;

【図4】面状コードヒータの構成を示す断面図である。FIG. 4 is a cross-sectional view illustrating a configuration of a planar cord heater.

【符号の説明】[Explanation of symbols]

1…生ごみ処理装置、2…筐体、3…生ごみ処理槽、4
…撹拌羽根、5…回転軸、6…面状コードヒータ、60
…環境温度センサ。
DESCRIPTION OF SYMBOLS 1 ... Garbage processing apparatus, 2 ... Housing, 3 ... Garbage processing tank, 4
... stirring blades, 5 ... rotating shaft, 6 ... planar cord heater, 60
... environmental temperature sensor.

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】撹拌羽根と換気装置を有する生ごみ処理槽
内におがくず,もみがら、等の基材と好気性バクテリア
とを入れ、調理くずや食べ残し等の生ごみを投入して撹
拌することにより、好気性バクテリアの働きで生ごみを
分解処理して減量する厨芥処理機において、 前記生ごみ処理槽の外周面に面状ヒータを貼り付けた構
成の保温ヒータと環境温度を測定する外気温度センサと
を設け、前記生ごみ処理槽に使用者が生ごみを投入した
時から3〜5時間の間の基材の発酵温度が低い期間の
み、環境温度より高い発熱温度で保温ヒータを働かせ
て、水分の蒸発促進による基材の水分率低減とバクテリ
アの活性化を図ったことを特徴とする厨芥処理機。
1. A garbage disposal tank having a stirring blade and a ventilation device, a substrate such as sawdust, rice husk, etc. and an aerobic bacterium are put into the garbage disposal tank, and garbage such as cooking waste and leftover food is charged and stirred. Thus, in a kitchen waste treatment machine that decomposes and reduces garbage by the action of aerobic bacteria, a warming heater having a configuration in which a planar heater is attached to the outer peripheral surface of the garbage disposal tank and an outside air for measuring environmental temperature A temperature sensor is provided, and only during a period in which the fermentation temperature of the base material is low for a period of 3 to 5 hours from the time when the user puts the garbage into the garbage processing tank, the warming heater is operated at an exothermic temperature higher than the ambient temperature. A kitchen waste treatment machine characterized by reducing the moisture content of the base material and activating bacteria by accelerating the evaporation of moisture.
【請求項2】請求項1において、 処理槽の保温ヒータの動作開始のタイミングである使用
者が生ごみを投入したことを知る手段として、投入口蓋
の開閉動作に連動してオン−オフするドアスイッチの開
閉動作をもって判断するようにしたことを特徴とする厨
芥処理機。
2. A door which turns on and off in conjunction with an opening / closing operation of an input lid as a means for knowing that a user has input garbage at the timing of starting operation of a heat retaining heater of a processing tank. A garbage disposal machine characterized in that a judgment is made based on an opening and closing operation of a switch.
【請求項3】請求項1において、 一旦保温ヒータが動作を開始した初期の間は、投入口蓋
の開閉動作があっても無視し、保温ヒータの動作時間の
延長につながる動作指示を行わないようにして、必要以
上の長時間に渡って保温ヒータが働くことによる無駄な
電力消費を防ぐようにしたことを特徴とする厨芥処理
機。
3. The method according to claim 1, wherein during the initial period in which the heat retaining heater starts to operate, the opening / closing operation of the charging lid is ignored, and an operation instruction leading to extension of the operation time of the heat retaining heater is not issued. A garbage disposal machine characterized in that wasteful power consumption due to the operation of the heat retention heater for an unnecessarily long time is prevented.
【請求項4】請求項1において、 一旦保温ヒータが動作した後は、所定の動作時間が終了
するまで、投入口蓋の開閉動作があっても、保温ヒータ
の動作時間の延長につながる動作指示を行わないように
して、必要以上の長時間に渡って保温ヒータが働くこと
による無駄な電力消費を防ぐようにしたことを特徴とす
る厨芥処理機。
4. The method according to claim 1, wherein once the heat retaining heater has been operated, an operation instruction leading to an extension of the operation time of the heat retaining heater is provided even if the opening / closing operation of the charging lid is performed until a predetermined operation time is completed. A garbage disposer characterized by preventing wasteful power consumption due to the operation of the heat retention heater for an unnecessarily long time by not performing the operation.
【請求項5】請求項1において、 保温ヒータの一日当たりの総動作時間を制限し、電力消
費を押さえるために、一日当たりの保温ヒータの動作回
数を制限したことを特徴とする厨芥処理機。
5. The garbage disposal machine according to claim 1, wherein the number of times of operation of the heat retaining heater per day is limited in order to limit the total operation time per day of the heat retaining heater and to suppress power consumption.
【請求項6】請求項5において、 一日の保温ヒータの動作回数を制限する手段として、保
温ヒータが所定時間の動作を終了した後の一定の時間の
間、投入口蓋の開閉動作があっても、保温ヒータを作動
させないようにしたことを特徴とする厨芥処理機。
6. The method according to claim 5, wherein the means for limiting the number of times of operation of the heat retaining heater per day includes opening and closing operation of the charging port lid for a predetermined time after the heat retaining heater has completed operation for a predetermined time. A kitchen waste treatment machine characterized by not operating the heat retention heater.
JP9010913A 1997-01-24 1997-01-24 Garbage treating machine Withdrawn JPH10202230A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9010913A JPH10202230A (en) 1997-01-24 1997-01-24 Garbage treating machine

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9010913A JPH10202230A (en) 1997-01-24 1997-01-24 Garbage treating machine

Publications (1)

Publication Number Publication Date
JPH10202230A true JPH10202230A (en) 1998-08-04

Family

ID=11763516

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9010913A Withdrawn JPH10202230A (en) 1997-01-24 1997-01-24 Garbage treating machine

Country Status (1)

Country Link
JP (1) JPH10202230A (en)

Similar Documents

Publication Publication Date Title
JPH10202230A (en) Garbage treating machine
JP2002159939A (en) Garbage treatment device
JP3729088B2 (en) Garbage processing machine
JP2003275717A (en) Waste treating apparatus
JP4009012B2 (en) Garbage decomposition and extinguishing machine with disposer using porous inorganic decomposition media
JP3238042B2 (en) Garbage processing machine
JP3674100B2 (en) Garbage decomposition processing equipment
KR100216207B1 (en) A food garbage treating apparatus with inputting and drying structure
JPH09132490A (en) Organic matter treating device
JP2881429B2 (en) Garbage processing machine
JPH10151431A (en) Garbage disposer
JPH05221765A (en) Ventilating method in composting device of domestic garbage
JP3104777B2 (en) Garbage disposal equipment
KR0172909B1 (en) Domestic refuse disposal system
JPH07290029A (en) Garbage disposal machine
JPH11151473A (en) Agitator of garbage disposal device
JPH10225673A (en) Garbage disposal apparatus
JPH07204613A (en) Garbage disposer
JPH11128889A (en) Garbage disposal machine
JPS63185498A (en) Garbage treating machine
JPH09225438A (en) Garbage processing device
JPH09124386A (en) Treating device for house garbage
JPH0824826A (en) Garbage treatment machine
KR19980062096U (en) Fast Food Waste Disposal Device
JPH08224562A (en) Garbage treatment apparatus

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20040123

RD02 Notification of acceptance of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7422

Effective date: 20040123

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20050623

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20050830

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20051031

RD02 Notification of acceptance of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7422

Effective date: 20060512

RD04 Notification of resignation of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7424

Effective date: 20060512

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20070410

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20070528

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20070626

A761 Written withdrawal of application

Free format text: JAPANESE INTERMEDIATE CODE: A761

Effective date: 20070820