JP2000325912A - Method and apparatus for automatically controlling operation of garbage treatment machine - Google Patents

Method and apparatus for automatically controlling operation of garbage treatment machine

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Publication number
JP2000325912A
JP2000325912A JP11135930A JP13593099A JP2000325912A JP 2000325912 A JP2000325912 A JP 2000325912A JP 11135930 A JP11135930 A JP 11135930A JP 13593099 A JP13593099 A JP 13593099A JP 2000325912 A JP2000325912 A JP 2000325912A
Authority
JP
Japan
Prior art keywords
temperature
garbage
processing tank
gas
drying
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.)
Pending
Application number
JP11135930A
Other languages
Japanese (ja)
Inventor
Hirohide Nakao
弘英 中尾
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.)
Jidosha Buhin Kogyo Co Ltd
Original Assignee
Jidosha Buhin Kogyo 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 Jidosha Buhin Kogyo Co Ltd filed Critical Jidosha Buhin Kogyo Co Ltd
Priority to JP11135930A priority Critical patent/JP2000325912A/en
Publication of JP2000325912A publication Critical patent/JP2000325912A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To set up the time of completion of garbage drying surely irrespective of a difference in outside air temperature or the specifications of a condenser and a heater. SOLUTION: In an automatic operation control method for a garbage treatment machine 1 equipped with a treatment tank 2 for agitating/drying garbage while heating it, a circulation passage 4 having a blower 3 for sucking/ circulating ambient gas in the tank 2, a condenser 5 which is installed upstream from the blower 3, cools the ambient gas F, and condenses steam in the gas F, and a gas-liquid separation tank 6 which is installed between the condenser 5 and the blower 3 and separates the gas from the condensed liquid by gravity, the temperature of the bottom surface of the tank 2 is detected, and a drying end time is decided from the variation in the bottom surface temperature.

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、乾燥・
固化させる生ゴミ処理機に係り、特に、処理槽に投入す
る外気温或いはコンデンサやヒータの仕様の相違にかか
わりなく乾燥終了時間を決定できる生ゴミ処理機の自動
運転制御方法及びその装置に関するものである。
BACKGROUND OF THE INVENTION The present invention relates to a method of drying garbage.
The present invention relates to a garbage disposal machine to be solidified, and more particularly to an automatic operation control method and an apparatus for a garbage disposal machine capable of determining a drying end time irrespective of an outside temperature to be charged into a treatment tank or a difference in specifications of a condenser and a heater. is there.

【0002】[0002]

【従来の技術】飲食店や家庭等において厨房から出る水
分の多い生ゴミ(野菜クズ、残飯等)を乾燥させて処理
する生ゴミ処理機は、生ゴミを、そのまま加熱したので
は、周囲に臭気が漏れるため、生ゴミを加熱する処理槽
に、ガスの循環路を接続し、処理槽内の雰囲気ガスを吸
引し、雰囲気ガス中の蒸気をコンデンサで冷却して凝縮
させると共に気液分離器に通して気液分離し、ガス分を
再度処理槽に循環することで、消臭しながら生ゴミを乾
燥し、生ゴミを最終的にサラサラ状態或いはサラサラだ
が多少油っぽい状態まで乾燥するようになっている。
2. Description of the Related Art A garbage disposer for drying and treating garbage (vegetable waste, garbage, etc.) having a large amount of water from a kitchen in a restaurant or at home uses a garbage disposer which is heated as it is. The gas circulation path is connected to the processing tank that heats garbage because the odor leaks, the atmospheric gas in the processing tank is sucked, the vapor in the atmospheric gas is cooled by a condenser and condensed, and the gas-liquid separator is used. To separate the gas and liquid, and circulate the gas again to the treatment tank to dry the garbage while deodorizing, so that the garbage is finally dried to a smooth state or a smooth but slightly oily state It has become.

【0003】ところで、この生ゴミ処理機で、生ゴミを
最終的にサラサラ状態或いはサラサラだが多少油っぽい
状態まで乾燥すべく自動制御する場合、従来は、本発明
者が特願平10−370561号において提案したよう
に、処理槽からコンデンサに至る循環路に温度センサを
設け、その循環路を通る蒸気の温度で終了時間を決定す
るようにしていた。
By the way, when the garbage is automatically controlled by this garbage disposer to finally dry the garbage to a smooth state or a smooth but somewhat oily state, the present inventor has conventionally proposed Japanese Patent Application No. 10-370561. As proposed in the above publication, a temperature sensor is provided in the circulation path from the processing tank to the condenser, and the end time is determined by the temperature of the steam passing through the circulation path.

【0004】具体的には図6に示すように、蒸気の温度
が、約100℃の一定温度から急激に降下(90℃に降
下)するまでの蒸発乾燥時間Aをカウントし、その蒸発
乾燥時間Aに応じて、その蒸発乾燥時間Aから運転終了
までの固形化時間Bを算出して、乾燥終了時間を決定す
るようになっていた。
More specifically, as shown in FIG. 6, the evaporative drying time A until the steam temperature suddenly drops (falls to 90 ° C.) from a constant temperature of about 100 ° C. is counted. According to A, the solidification time B from the evaporative drying time A to the end of the operation is calculated to determine the drying end time.

【0005】[0005]

【発明が解決しようとする課題】しかしながら、上述の
ように循環路を通る蒸気の温度で終了時間を決定するの
では、外気温によって、蒸気温度が基準温度(90℃)
まで低下する時間にバラツキが発生するため、乾燥終了
時間が正確に出ない場合があった。
However, when the end time is determined by the temperature of the steam passing through the circulation path as described above, the steam temperature is set to the reference temperature (90 ° C.) depending on the outside air temperature.
In some cases, the time required for drying to vary varies, so that the drying end time may not be accurate.

【0006】また、凝縮水の温度を下げてその臭気を低
減させるべく、コンデンサの能力を上げたり、ユーザの
電力事情を考慮して定格電力を減らして、ヒータ能力を
下げる場合には、A期間の温度が100℃より低くなる
ので、基準温度を変更する必要があった。
In order to lower the temperature of the condensed water to reduce its odor, the capacity of the condenser is increased, or the rated power is reduced in consideration of the power situation of the user to reduce the heater capacity. Temperature was lower than 100 ° C., so that the reference temperature had to be changed.

【0007】そこで本発明は、上記問題を解決すべく案
出されたものであって、その目的は、外気温或いはコン
デンサやヒータの仕様の相違にかかわりなく、生ゴミの
乾燥終了時間を確実に設定できる生ゴミ処理機の自動運
転制御装置を提供することにある。
Accordingly, the present invention has been devised to solve the above-mentioned problem, and an object of the present invention is to ensure that the end time of garbage drying is completed irrespective of the outside air temperature or the difference in the specifications of the condenser and the heater. An object of the present invention is to provide an automatic operation control device for a garbage disposal machine that can be set.

【0008】[0008]

【課題を解決するための手段】前記課題を解決すべく、
請求項1の発明は、生ゴミを加熱しながら撹拌して乾燥
させる処理槽と、該処理槽内の雰囲気ガスを吸引して循
環させるブロワを有する循環路と、該循環路の上記ブロ
ワの上流側に設けられ上記雰囲気ガスを冷却して雰囲気
ガス内の蒸気を凝縮させるコンデンサと、該コンデンサ
と上記ブロワ間に設けられ気体と凝縮された液体とを重
力分離する気液分離槽とを備えた生ゴミ処理機の自動運
転制御方法において、上記処理槽の底面の温度を検出す
ると共にその底面温度の変化から乾燥終了時間を決定す
る生ゴミ処理機の自動運転制御方法である。
In order to solve the above-mentioned problems,
The invention of claim 1 is a processing tank for stirring and drying garbage while heating, a circulation path having a blower for sucking and circulating atmospheric gas in the processing tank, and an upstream of the blower in the circulation path. A condenser for cooling the atmospheric gas and condensing vapor in the atmospheric gas, and a gas-liquid separation tank provided between the condenser and the blower and gravity-separating the gas and the condensed liquid. An automatic operation control method for a garbage disposal machine, wherein the temperature of the bottom surface of the processing tank is detected and the drying end time is determined from a change in the bottom surface temperature.

【0009】上記方法によれば、処理槽の底面の温度を
検出すると共にその底面温度の変化から乾燥終了時間を
決定することで、外気温或いはコンデンサやヒータの仕
様の相違に影響されることなく、生ゴミの乾燥終了時間
を確実に設定することができる。
According to the above method, by detecting the temperature of the bottom surface of the processing tank and determining the drying end time from the change in the bottom surface temperature, the temperature is not affected by the outside air temperature or the difference in the specifications of the condenser and the heater. In addition, the end time of drying the garbage can be reliably set.

【0010】請求項2の発明は、上記処理槽の運転開始
からその処理槽の底面の温度を検出すると共に運転時間
を積算し、運転開始から検出温度が約90℃の一定温度
から急激に上昇するまでの蒸発乾燥時間をカウントし、
その時間を基準として、乾燥終了時間を決定すると共に
処理槽の運転を停止する請求項1記載の生ゴミ処理機の
自動運転制御方法である。
According to a second aspect of the present invention, the temperature of the bottom of the processing tank is detected from the start of operation of the processing tank and the operation time is integrated, and the detected temperature rises rapidly from a constant temperature of about 90 ° C. from the start of operation. Count the evaporative drying time until
2. The automatic operation control method for a garbage disposal machine according to claim 1, wherein the drying end time is determined based on the time and the operation of the processing tank is stopped.

【0011】請求項3の発明は、生ゴミを加熱しながら
撹拌して乾燥させる処理槽と、該処理槽内の雰囲気ガス
を吸引して循環させるブロワを有する循環路と、該循環
路の上記ブロワの上流側に設けられ上記雰囲気ガスを冷
却して雰囲気ガス内の蒸気を凝縮させるコンデンサと、
該コンデンサと上記ブロワ間に設けられ気体と凝縮され
た液体とを重力分離する気液分離槽とを備えた生ゴミ処
理機において、上記処理槽の底面に設けられた温度セン
サと、処理槽の運転開始から上記温度センサの温度を検
出すると共に運転時間を積算し、運転開始から温度セン
サの検出温度が、約90℃の一定温度から急激に上昇す
るまでの蒸発乾燥時間をカウントし、その時間を基準と
して、乾燥終了時間を決定すると共に処理槽の運転を停
止する運転制御手段とを備えた生ゴミ処理機である。
The invention according to claim 3 is a processing tank for heating and stirring the garbage while drying it, a circulation path having a blower for sucking and circulating the atmospheric gas in the processing tank, and A condenser provided on the upstream side of the blower for cooling the atmosphere gas and condensing vapor in the atmosphere gas;
In a garbage disposer provided between the condenser and the blower and provided with a gas-liquid separation tank for gravity-separating a gas and a condensed liquid, a temperature sensor provided on a bottom surface of the processing tank; The temperature of the temperature sensor is detected from the start of operation and the operation time is integrated, and the evaporative drying time from the start of operation until the temperature detected by the temperature sensor rapidly rises from a constant temperature of about 90 ° C. is counted. And an operation control means for determining the drying end time and stopping the operation of the processing tank with reference to the above.

【0012】[0012]

【発明の実施の形態】以下、本発明の実施の形態を添付
図面に従って説明する。
Embodiments of the present invention will be described below with reference to the accompanying drawings.

【0013】図1は本発明に係る生ゴミ処理機の実施の
形態を示した全体構成図、図2は処理槽と制御装置を示
した要部拡大図、図3は処理槽の底面温度及び側面温度
の経時変化を示したグラフである。
FIG. 1 is an overall configuration diagram showing an embodiment of a garbage processing machine according to the present invention, FIG. 2 is an enlarged view of a main part showing a processing tank and a control device, and FIG. It is the graph which showed the temporal change of the side surface temperature.

【0014】まず、図1によって、本発明に係る生ゴミ
処理機の全体の構成を説明する。
First, the overall configuration of a garbage disposal machine according to the present invention will be described with reference to FIG.

【0015】図示するように、上記生ゴミ処理機1は、
生ゴミRを加熱して乾燥させる処理槽2と、処理槽2の
内部の雰囲気ガスFを吸引して循環させて再度処理槽2
内に戻すブロワ3を有する循環路4とからなり、循環路
4のブロワ3の上流側には、上記雰囲気ガスFを冷却し
て雰囲気ガスF内の蒸気を凝縮させるコンデンサ5が接
続され、コンデンサ5と上記ブロワ3との間に、気体と
凝縮液とを重力にて気液分離する気液分離槽6が設けら
れている。
As shown in FIG.
A processing tank 2 for heating and drying the garbage R, and an atmosphere gas F inside the processing tank 2 is sucked and circulated to re-process the processing tank 2.
A circulation path 4 having a blower 3 returning to the inside is connected to a condenser 5 that cools the atmosphere gas F and condenses the vapor in the atmosphere gas F on the upstream side of the blower 3 in the circulation path 4. Between the blower 5 and the blower 3, there is provided a gas-liquid separation tank 6 for separating gas and condensate from each other by gravity.

【0016】処理槽2は、有底筒体状に形成された容器
7に加熱コイル8がこれを覆うように設けられている。
容器7の内方には、投入された生ゴミRを粉砕、撹拌す
るための撹拌部材9が設けられている。容器7の上部開
口には蓋体11が設けられ、生ゴミRを投入した後はこ
の蓋体11を閉じることにより処理槽2内を密閉状態に
保つようになっている。
The processing tank 2 is provided so that a heating coil 8 covers a container 7 formed in a bottomed cylindrical shape.
Inside the container 7, a stirring member 9 for crushing and stirring the charged garbage R is provided. A lid 11 is provided at the upper opening of the container 7, and after the garbage R is charged, the lid 11 is closed to keep the inside of the processing tank 2 in a sealed state.

【0017】撹拌部材9は、処理槽2の軸心の位置に沿
って起立された回転軸12と、この回転軸12に周方向
及び軸方向に等間隔で放射状に取り付けられた複数のブ
レード14とを備えている。また、撹拌部材9にはこれ
を回転させるためのモータ15が備えられ、減速機16
を介して回転軸12に連結されている。
The stirring member 9 includes a rotating shaft 12 erected along the axis of the processing tank 2 and a plurality of blades 14 radially attached to the rotating shaft 12 at equal intervals in the circumferential and axial directions. And Further, the stirring member 9 is provided with a motor 15 for rotating the stirring member 9 and a speed reducer 16.
Is connected to the rotating shaft 12 through the shaft.

【0018】処理槽2の上部には、その内部の雰囲気ガ
スFの出口となる開口部17が形成されており、この開
口部17には循環路4の一部を構成する吸引管25が接
続されている。
An opening 17 serving as an outlet for the atmospheric gas F inside the processing tank 2 is formed in the upper part of the processing tank 2, and a suction pipe 25 constituting a part of the circulation path 4 is connected to the opening 17. Have been.

【0019】循環路4内のコンデンサ5は、蛇行して形
成された配管18に板状の放熱フィン19が設けられて
形成され、そのコンデンサ5内の雰囲気ガスFを空冷す
るための冷却ファン21が設けられる。
The condenser 5 in the circulation path 4 is formed by providing plate-shaped radiation fins 19 on a meandering pipe 18, and a cooling fan 21 for air-cooling the atmosphere gas F in the condenser 5. Is provided.

【0020】気液分離槽6は、密閉された箱状に形成さ
れており、その側面上部にはコンデンサ5によって冷却
された雰囲気ガスFが流入するガス流入口22が形成さ
れ、上部には気体Gを流出させる気体流出口23が形成
され、底部には凝縮液Wを下方に排出する液体排出口2
4が形成されている。
The gas-liquid separation tank 6 is formed in a closed box shape. A gas inlet 22 through which the atmospheric gas F cooled by the condenser 5 flows is formed in the upper part of the side surface. A gas outlet 23 for discharging G is formed, and a liquid outlet 2 for discharging condensate W downward is formed at the bottom.
4 are formed.

【0021】そして、気液分離槽6の下流側となる気体
流出口23の上部には、ブロワ3が設けられている。こ
のブロワ3の下流側には循環路4の一部を構成する流入
管26が設けられており、流入管26は、処理槽2の上
部に形成された気体の入口となる開口部27に接続され
ている。
The blower 3 is provided above the gas outlet 23 downstream of the gas-liquid separation tank 6. Downstream of the blower 3 is provided an inflow pipe 26 that constitutes a part of the circulation path 4, and the inflow pipe 26 is connected to an opening 27 formed at the upper part of the processing tank 2 and serving as a gas inlet. Have been.

【0022】上記気液分離槽6の底部には、上記循環路
4内の内圧を設定範囲内に保持しながら液体を排出する
と共に、循環路4内が負圧になったとき外気を導入する
略U字状の圧力補償ドレン管31が接続される。圧力補
償ドレン管31は、一端が気液分離槽6の液体排出口2
4に接続され、他端が外部に開口されると共にその間に
U字状の湾曲部32が形成され、湾曲部32に気液分離
槽31からの液を溜めその水頭圧Hで循環路4内の圧力
を補償するようになっている。
At the bottom of the gas-liquid separation tank 6, the liquid is discharged while maintaining the internal pressure in the circulation path 4 within a set range, and outside air is introduced when the pressure in the circulation path 4 becomes negative. A substantially U-shaped pressure compensation drain pipe 31 is connected. One end of the pressure compensation drain pipe 31 is connected to the liquid discharge port 2 of the gas-liquid separation tank 6.
4, the other end of which is open to the outside and a U-shaped curved portion 32 is formed therebetween. The liquid from the gas-liquid separation tank 31 is stored in the curved portion 32 and the water head pressure H in the circulation path 4. Pressure is compensated.

【0023】この圧力補償ドレン管31には、その外周
部に帯状のリボンヒータ33が巻き付けられており、寒
冷期に内部の液体が凍結しないように加熱するようにな
っている。
A band-shaped ribbon heater 33 is wound around the pressure compensating drain tube 31 so as to heat the liquid so that the liquid inside does not freeze during the cold season.

【0024】この生ゴミ処理機での生ゴミ処理は、生ゴ
ミを水切りを行って処理槽2に投入し、加熱コイル8で
加熱し、同時にブロワ3で処理槽2内の雰囲気ガスFを
循環路で循環しながら乾燥処理を行う。生ゴミから発生
する蒸気は雰囲気ガスFとともにコンデンサ5で冷却さ
れて凝縮され、気液分離槽6で液分が除去されてガス分
が流入管26より再度処理槽2内に戻される。
In the garbage disposal in this garbage disposal machine, garbage is drained, put into the treatment tank 2, heated by the heating coil 8, and at the same time, the atmosphere gas F in the treatment tank 2 is circulated by the blower 3. The drying process is performed while circulating in the road. The vapor generated from the garbage is cooled and condensed by the condenser 5 together with the atmospheric gas F, the liquid component is removed in the gas-liquid separation tank 6, and the gas component is returned to the processing tank 2 through the inflow pipe 26.

【0025】処理槽2内では撹拌部材9で撹拌されて粉
砕されながら徐々に水分が蒸発されて乾燥・固化され
る。乾燥の結果残った処理物は、処理槽2に形成された
排出口34から取り出されて、土中に埋められて肥料の
原料としてリサイクル利用されるか、或いは一般ゴミと
一緒に焼却処理される。
In the processing tank 2, the water is gradually evaporated while being agitated and pulverized by the agitating member 9 to be dried and solidified. The processed material remaining as a result of drying is taken out from the discharge port 34 formed in the processing tank 2 and buried in the soil to be recycled as a raw material for fertilizer, or incinerated together with general waste. .

【0026】本発明においては、処理槽2の容器7に、
その底面温度を検出する底面温度センサ35と側面温度
を検出する側面温度センサ36とが設けられ、また処理
槽2とコンデンサ5間の循環路4を構成する吸引管25
には、処理槽2からの雰囲気ガス温度(蒸気温度)を検
出する循環路温度センサ37が設けられており、これら
各温度センサ35,36,37の検出値が運転制御手段
38に入力される。
In the present invention, the container 7 of the processing tank 2
A bottom surface temperature sensor 35 for detecting the bottom surface temperature and a side surface temperature sensor 36 for detecting the side surface temperature are provided, and a suction pipe 25 forming a circulation path 4 between the processing tank 2 and the condenser 5.
Is provided with a circulation path temperature sensor 37 for detecting the ambient gas temperature (steam temperature) from the processing tank 2, and the detection values of these temperature sensors 35, 36, 37 are input to the operation control means 38. .

【0027】図2に示すように、運転制御手段38に
は、上記各温度センサ35,36,37に接続され、運
転開始時にブロワ3、モータ15、冷却ファン21を起
動し、同時に加熱コイル8に通電し、その運転中、底面
温度センサ35及び側面温度センサ36の検出値に応じ
て加熱コイル8をON・OFF制御して処理槽2内の温
度を制御するシーケンサ41が設けられている。
As shown in FIG. 2, the operation control means 38 is connected to each of the temperature sensors 35, 36, and 37, starts the blower 3, the motor 15, and the cooling fan 21 at the start of operation, and simultaneously activates the heating coil 8 And a sequencer 41 for controlling the temperature in the processing tank 2 by controlling ON / OFF of the heating coil 8 according to the detection values of the bottom surface temperature sensor 35 and the side surface temperature sensor 36 during the operation.

【0028】このシーケンサ41には温調器43が接続
されている。温調器43には、各部の温度を表示する表
示部44と、設定温度を調整する調整スイッチ45とが
設けられている。
A temperature controller 43 is connected to the sequencer 41. The temperature controller 43 is provided with a display section 44 for displaying the temperature of each section and an adjustment switch 45 for adjusting the set temperature.

【0029】本発明は、処理槽2の底面の温度を検出す
ると共にその底面温度の変化から乾燥終了時間を決定す
ることを特徴とする。
The present invention is characterized in that the temperature of the bottom surface of the processing tank 2 is detected and the drying end time is determined from the change in the bottom surface temperature.

【0030】以下、図3の処理槽の底面温度及び側面温
度の経時変化を示したグラフに沿って、具体的な自動運
転制御方法を説明する。
Hereinafter, a specific automatic operation control method will be described with reference to the graph of FIG. 3 showing the change over time of the bottom surface temperature and the side surface temperature of the processing tank.

【0031】加熱コイル8に通電後、底面温度(図中破
線にて示す)は、一旦90℃前後まで上昇し、処理槽2
内の生ゴミが一様の流動状態にある内はこの状態を保
つ。これは、生ゴミの含水量が多く、処理槽2の壁面か
ら生ゴミへの熱伝導率が大きいため、生ゴミに多くの熱
量が伝えられ、底面は一定温度を保つためである。
After energizing the heating coil 8, the bottom surface temperature (shown by a broken line in the figure) once rises to around 90 ° C.
This state is maintained while the garbage inside is in a uniform flowing state. This is because the water content of the garbage is large and the heat conductivity from the wall surface of the processing tank 2 to the garbage is large, so that a large amount of heat is transmitted to the garbage and the bottom surface is kept at a constant temperature.

【0032】なお、熱伝導量Q(kcal/h)は以下
の式によって求められる。
The thermal conductivity Q (kcal / h) is obtained by the following equation.

【0033】Q=S・h・(TW −TR ) (但し、S:伝熱面積(m2 )、h:熱伝達率(kca
l/m2 ・h・℃)、TW :壁面温度(℃)、TR :壁
面近傍の生ゴミの温度(℃)) そして、一定時間経過して、生ゴミの水分が蒸発してそ
の含水量が少なくなると共に生ゴミの固形化によって壁
面との間に空気が介在することによって、熱伝達率が小
さくなり、底面温度が急激に上昇する。その温度が14
0℃まで上昇すると、シーケンサ41によって加熱コイ
ル8の通電のON・OFFが繰り返され、130℃から
140℃の間で維持される。
Q = S · h · (T W −T R ) (where S: heat transfer area (m 2 ), h: heat transfer coefficient (kca)
l / m 2 · h · ° C.), T W : wall surface temperature (° C.), T R : temperature of garbage near the wall surface (° C.). As the water content decreases and air is interposed between the garbage and the wall surface due to solidification of the garbage, the heat transfer coefficient decreases and the bottom surface temperature rises rapidly. The temperature is 14
When the temperature rises to 0 ° C., ON / OFF of the energization of the heating coil 8 is repeated by the sequencer 41, and is maintained between 130 ° C. and 140 ° C.

【0034】上記温度の経時変化の内、検出温度が約9
0℃の一定温度から急激に上昇する時点、例えば検出温
度が110℃を越える時点をシーケンサ41によって検
知して、これを従来技術で説明した蒸発乾燥時間Aとし
てカウントし、その時間を基準として、その蒸発乾燥時
間Aから運転終了までの固形化時間Bを算出して、乾燥
終了時間を決定する。
Of the above-mentioned temporal changes in temperature, the detected temperature is about 9
A point at which the temperature suddenly rises from a constant temperature of 0 ° C., for example, a point at which the detected temperature exceeds 110 ° C. is detected by the sequencer 41, and this is counted as the evaporative drying time A described in the related art. The solidification time B from the evaporative drying time A to the end of the operation is calculated to determine the drying end time.

【0035】なお、側面温度(図中実線にて示す)は、
一旦100℃前後まで上昇し、一定時間この状態を保っ
た後、急激に上昇して、その温度が140℃まで上昇す
ると、シーケンサ41によって加熱コイル8の通電のO
N・OFFが繰り返され、130℃から140℃の間で
維持されるが、生ゴミの容量によって、その経時変化に
若干のばらつきがあるため、本発明では安定性の高い底
面温度の変化から乾燥終了時間を決定するようになって
いる。
The side temperature (shown by a solid line in the figure) is
Once the temperature rises to about 100 ° C., and after maintaining this state for a certain period of time, the temperature rises sharply, and when the temperature rises to 140 ° C., the sequencer 41 turns the heating coil 8 on and off.
N · OFF is repeated and maintained between 130 ° C. and 140 ° C. However, the amount of garbage varies slightly with time. The end time is determined.

【0036】次に、固形化時間Bの算出法を説明する。Next, a method of calculating the solidification time B will be described.

【0037】図4は、横軸を底面温度が110℃を越え
るまでの時間(蒸発乾燥時間A)に対して任意に固形化
時間Bを選んで乾燥処理したときのデータを示し、□印
は、乾燥されてサラサラした状態、或いはサラサラだが
多少油っぽい状態で良好な乾燥・固化がえられたものを
示し、■印は、固化が不十分でベタベタ乃至ドロドロし
た状態で乾燥・固化が不十分なものを示している。
FIG. 4 shows the data when the solidification time B is arbitrarily selected for the time until the bottom surface temperature exceeds 110 ° C. (evaporation drying time A) on the horizontal axis and the drying treatment is performed. Indicates that the product was dried and smooth, or that it was dry and solidified, but was slightly oily and that it had good drying and solidification. Shows enough.

【0038】図4のデータから明らかなように、乾燥固
化が良好な□印では、蒸発乾燥時間Aと固形化時間Bと
に相関があり、蒸発乾燥時間Aが同じでも■印のように
固化時間Bが少ないものと区別でき、かつ蒸発乾燥時間
Aが相違しても、その蒸発乾燥時間Aに対して最適な固
形化時間Bは一定の関係があることが分かる。
As is clear from the data in FIG. 4, in the case of □ which shows good drying and solidification, there is a correlation between the evaporative drying time A and the solidification time B. It can be seen that even if the time B is short, and the evaporation drying time A is different, the optimum solidification time B has a certain relationship with the evaporation drying time A.

【0039】また、図5は、処理槽2に投入した生ゴミ
量と最適な乾燥終了時間(A+B)の関係を示したもの
で、生ゴミ20〜60kgに種々変えて乾燥・固化した
ところ処理量と乾燥終了時間に比例関係があることが認
められた。
FIG. 5 shows the relationship between the amount of garbage charged into the processing tank 2 and the optimal drying end time (A + B). It was found that there was a proportional relationship between the amount and the drying end time.

【0040】そこで、この蒸発乾燥AからBを図4の直
線Lから求めると直線Lの傾きk1は、0.25、切片k2
は1.8(Hr)であり、従って直線Lの式は、 B=0.25A+1.8 (Hr) で表せることとなる。
Therefore, when the evaporation and drying A to B are obtained from the straight line L in FIG. 4, the slope k1 of the straight line L is 0.25 and the intercept k2
Is 1.8 (Hr), and therefore, the equation of the straight line L can be expressed by B = 0.25A + 1.8 (Hr).

【0041】この図4で求めた式は、食堂やレストラン
から出る一般的、標準的な生ゴミであり、単一処理物
(例えば、野菜だけ、魚のあらだけ、オカラだけ、芝生
の芝だけ)では種々傾きk1と切片k2の値は異なったもの
となる。
The formula obtained in FIG. 4 is a general and standard garbage discharged from a dining room or a restaurant, and is a single processed product (eg, only vegetables, only fish, only okara, only lawn grass). Then, the values of the various slopes k1 and the intercepts k2 are different.

【0042】従って、上記式を B=k1A+k2 (Hr) とし、ゴミ種によって係数k1,k2を変更できるように運
転制御手段38にゴミ種による係数の変更ができるよう
にする。
Therefore, the above equation is set as B = k1A + k2 (Hr), and the operation control means 38 can change the coefficient according to the type of dust so that the coefficients k1 and k2 can be changed according to the type of dust.

【0043】この場合、ゴミ種に応じて、k1を、0.1
〜0.3の範囲で、k2を、0〜2.0の範囲で、変える
ことで、全ての生ゴミのゴミ種に応じた乾燥・固化の最
適な乾燥終了時間(A+B)を設定することが可能とな
る。
In this case, k1 is set to 0.1 according to the kind of garbage.
By setting k2 in the range of 0.3 to 0.3 and changing k2 in the range of 0 to 2.0, the optimal drying end time (A + B) for drying and solidifying according to the type of all garbage is set. Becomes possible.

【0044】以上のように、本発明においては、処理槽
2の底面温度が90℃から急激に上昇する時期(例えば
110℃)を運転制御手段38が検出値から求めると共
に運転開始からその時期までの時間をカウントして蒸発
乾燥時間Aを求め、その求めた蒸発乾燥時間Aから残り
の固形化時間Bを算出し、処理開始からA+B(時間)
となったときに処理槽2内の加熱コイル8の通電を停止
して、処理を終了させる。
As described above, in the present invention, the time when the bottom surface temperature of the processing tank 2 rapidly rises from 90 ° C. (for example, 110 ° C.) is obtained from the detected value by the operation control means 38 and from the start of operation to the time. And the remaining solidification time B is calculated from the obtained evaporation and drying time A, and A + B (time) from the start of the treatment.
Then, the power supply to the heating coil 8 in the processing tank 2 is stopped to terminate the processing.

【0045】このように底面温度の変化から蒸発乾燥時
間Aを決定したことによって、循環路4を介さずに処理
槽2内の生ゴミの状態を検知でき、外気温に影響される
ことがない。また、コンデンサやヒータの仕様の相違に
対しても設定温度を変更する必要はない。
As described above, the evaporative drying time A is determined from the change in the bottom surface temperature, so that the state of the garbage in the processing tank 2 can be detected without passing through the circulation path 4 and is not affected by the outside temperature. . Further, it is not necessary to change the set temperature even when the specifications of the condenser and the heater differ.

【0046】底面温度は、その変化量が大きく(90℃
から140℃で50℃もある)、その変化を容易に検知
できる。これによって、確実かつ正確に乾燥・固化が常
に良好な状態で自動運転を停止させることが可能とな
る。
The bottom surface temperature has a large variation (90 ° C.).
From 140 ° C to 50 ° C), the change can be easily detected. As a result, it is possible to reliably and accurately stop the automatic operation in a state where the drying and solidification are always good.

【0047】[0047]

【発明の効果】以上要するに本発明によれば、外気温或
いはコンデンサやヒータの仕様の相違にかかわりなく、
生ゴミの乾燥終了時間を確実に設定できるという優れた
効果を発揮する。
In summary, according to the present invention, regardless of the outside air temperature or the difference in the specifications of the condenser and the heater,
It has an excellent effect that the end time of drying garbage can be reliably set.

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

【図1】本発明に係る生ゴミ処理機の実施の形態を示し
た全体構成図である。
FIG. 1 is an overall configuration diagram showing an embodiment of a garbage processing machine according to the present invention.

【図2】処理槽と制御装置を示した要部拡大図である。FIG. 2 is an enlarged view of a main part showing a processing tank and a control device.

【図3】処理槽の底面温度及び側面温度の経時変化を示
したグラフである。
FIG. 3 is a graph showing a change with time of a bottom surface temperature and a side surface temperature of a processing tank.

【図4】蒸発乾燥時間と固形化時間との関係を示したグ
ラフである。
FIG. 4 is a graph showing the relationship between the evaporative drying time and the solidification time.

【図5】生ゴミ処理量と処理時間との関係を示したグラ
フである。
FIG. 5 is a graph showing a relationship between a garbage processing amount and a processing time.

【図6】コンデンサに至る蒸気温度の経時変化を示した
グラフである。
FIG. 6 is a graph showing a change over time of a steam temperature reaching a condenser.

【符号の説明】[Explanation of symbols]

1 生ゴミ処理機 2 処理槽 3 ブロワ 4 循環路 5 コンデンサ 6 気液分離槽 35 (底面)温度センサ 38 運転制御手段 DESCRIPTION OF SYMBOLS 1 Garbage processing machine 2 Processing tank 3 Blower 4 Circulation path 5 Condenser 6 Gas-liquid separation tank 35 (Bottom) temperature sensor 38 Operation control means

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 生ゴミを加熱しながら撹拌して乾燥させ
る処理槽と、該処理槽内の雰囲気ガスを吸引して循環さ
せるブロワを有する循環路と、該循環路の上記ブロワの
上流側に設けられ上記雰囲気ガスを冷却して雰囲気ガス
内の蒸気を凝縮させるコンデンサと、該コンデンサと上
記ブロワ間に設けられ気体と凝縮された液体とを重力分
離する気液分離槽とを備えた生ゴミ処理機の自動運転制
御方法において、上記処理槽の底面の温度を検出すると
共にその底面温度の変化から乾燥終了時間を決定するこ
とを特徴とする生ゴミ処理機の自動運転制御方法。
1. A processing tank for heating and stirring garbage while drying, a circulation path having a blower for sucking and circulating atmospheric gas in the processing tank, and a circulation path upstream of the blower in the circulation path. Garbage provided with a condenser for cooling the atmospheric gas and condensing the vapor in the atmospheric gas, and a gas-liquid separation tank provided between the condenser and the blower for gravity separation of the gas and the condensed liquid An automatic operation control method for a garbage processing machine, comprising: detecting a temperature of a bottom surface of the processing tank and determining a drying end time from a change in the bottom surface temperature.
【請求項2】 上記処理槽の運転開始からその処理槽の
底面の温度を検出すると共に運転時間を積算し、運転開
始から検出温度が約90℃の一定温度から急激に上昇す
るまでの蒸発乾燥時間をカウントし、その時間を基準と
して、乾燥終了時間を決定すると共に処理槽の運転を停
止する請求項1記載の生ゴミ処理機の自動運転制御方
法。
2. A process for detecting the temperature of the bottom surface of the processing tank from the start of operation of the processing tank and integrating the operation time, and evaporating and drying the temperature from the start of operation until the detected temperature rises rapidly from a constant temperature of about 90 ° C. 2. The automatic operation control method for a garbage disposal machine according to claim 1, wherein the time is counted, and based on the time, the drying end time is determined and the operation of the processing tank is stopped.
【請求項3】 生ゴミを加熱しながら撹拌して乾燥させ
る処理槽と、該処理槽内の雰囲気ガスを吸引して循環さ
せるブロワを有する循環路と、該循環路の上記ブロワの
上流側に設けられ上記雰囲気ガスを冷却して雰囲気ガス
内の蒸気を凝縮させるコンデンサと、該コンデンサと上
記ブロワ間に設けられ気体と凝縮された液体とを重力分
離する気液分離槽とを備えた生ゴミ処理機において、上
記処理槽の底面に設けられた温度センサと、処理槽の運
転開始から上記温度センサの温度を検出すると共に運転
時間を積算し、運転開始から温度センサの検出温度が、
約90℃の一定温度から急激に上昇するまでの蒸発乾燥
時間をカウントし、その時間を基準として、乾燥終了時
間を決定すると共に処理槽の運転を停止する運転制御手
段とを備えたことを特徴とする生ゴミ処理機。
3. A processing tank for stirring and drying the garbage while heating the garbage, a circulation path having a blower for sucking and circulating the atmospheric gas in the processing tank, and a circulation path upstream of the blower in the circulation path. Garbage provided with a condenser for cooling the atmospheric gas and condensing vapor in the atmospheric gas, and a gas-liquid separation tank provided between the condenser and the blower for gravity separation of the gas and the condensed liquid In the processing machine, the temperature sensor provided on the bottom surface of the processing tank, the temperature of the temperature sensor is detected from the start of the operation of the processing tank and the operation time is integrated, and the detected temperature of the temperature sensor from the start of the operation is:
Operation control means for counting the evaporative drying time from a constant temperature of about 90 ° C. to a sharp rise, determining a drying end time based on the time, and stopping the operation of the processing tank. And garbage processing machine.
JP11135930A 1999-05-17 1999-05-17 Method and apparatus for automatically controlling operation of garbage treatment machine Pending JP2000325912A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11135930A JP2000325912A (en) 1999-05-17 1999-05-17 Method and apparatus for automatically controlling operation of garbage treatment machine

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11135930A JP2000325912A (en) 1999-05-17 1999-05-17 Method and apparatus for automatically controlling operation of garbage treatment machine

Publications (1)

Publication Number Publication Date
JP2000325912A true JP2000325912A (en) 2000-11-28

Family

ID=15163180

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11135930A Pending JP2000325912A (en) 1999-05-17 1999-05-17 Method and apparatus for automatically controlling operation of garbage treatment machine

Country Status (1)

Country Link
JP (1) JP2000325912A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100747047B1 (en) 2006-05-02 2007-08-10 주식회사 두림코리아 Food waste disposal equipment

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100747047B1 (en) 2006-05-02 2007-08-10 주식회사 두림코리아 Food waste disposal equipment

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