JP2000189925A - Automatic operation controller for garbage disposal system - Google Patents

Automatic operation controller for garbage disposal system

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Publication number
JP2000189925A
JP2000189925A JP10370561A JP37056198A JP2000189925A JP 2000189925 A JP2000189925 A JP 2000189925A JP 10370561 A JP10370561 A JP 10370561A JP 37056198 A JP37056198 A JP 37056198A JP 2000189925 A JP2000189925 A JP 2000189925A
Authority
JP
Japan
Prior art keywords
time
temperature
drying
garbage
condenser
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
JP10370561A
Other languages
Japanese (ja)
Inventor
Hirohide Nakao
弘英 中尾
Toshiyuki Takahashi
俊行 高橋
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 JP10370561A priority Critical patent/JP2000189925A/en
Priority to KR1019990044332A priority patent/KR20000047528A/en
Publication of JP2000189925A publication Critical patent/JP2000189925A/en
Pending legal-status Critical Current

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  • Drying Of Solid Materials (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a controller capable of surely setting the time required for completion of garbage drying/solidification operation of the disposal system. SOLUTION: This disposal system is provided with: a heating vessel 2 for heating and drying garbage; a blower 3 for sucking and circulating an atmospheric gas within the heating vessel 2; a circulation passage 4 having the blower 3; a condenser 5 that is placed in a position upstream from the blower 3 of the circulation passage 4 and used for cooling the atmospheric gas to condense vapor in the atmospheric gas; and a gas-liquid separation vessel 6 that is placed in a position between the condenser 5 and the blower 3, of the circulation passage 4 and used for subjecting the uncondensed gas and condensed liquid, formed in the condenser 5, to gravity separation. In the disposal system, a temperature sensor 36 is fitted to the circulation passage 4 on the way from the heating vessel 2 to the condenser 5; and also, an operation control means 40 for detecting temperature of the circulation atmospheric gas from the start point of operation of the heating vessel 2 with the sensor 36, concurrently calculating the integrated operating time from the start point of the operation, counting the evaporation/drying time A from the start point of the operation to the point at which the detected temperature with the sensor 36 steeply drops from an about 100 deg.C constant temperature, determining the time required for drying, (A+B), accordingly to the evaporation/drying time A and stopping the operation of the heating vessel 2, is placed.

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、周囲に臭気を発生
させることなく生ゴミを、乾燥・固化させる生ゴミ処理
装置に係り、特に、加熱槽に投入する生ゴミの投入量の
大小にかかわりなく処理終了時間を決定できると共に消
臭させる生ゴミ処理装置の自動運転制御装置に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a garbage disposal apparatus for drying and solidifying garbage without generating odors around the garbage, and more particularly to a garbage disposal apparatus to be supplied to a heating tank. The present invention relates to an automatic operation control device of a garbage disposal device capable of determining a processing end time without causing the garbage to deodorize.

【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
する生ゴミ処理装置は、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、生ゴミを加熱する加熱
槽に、ガスの循環路を接続し、加熱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
を再度加熱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 processing garbage (vegetable waste, garbage, etc.) having a large amount of water from a kitchen in a restaurant or a home is a garbage disposal apparatus that heats garbage without heating. Because the odor leaks, a gas circulation path is connected to the heating tank that heats the garbage, the atmosphere gas in the heating tank is sucked, the vapor in the atmosphere gas is cooled by a condenser, condensed, and a gas-liquid separator is used. To separate gas and liquid, and circulate the gas to the heating tank again 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】[0003]

【発明が解決しようとする課題】ところで、この生ゴミ
処理装置で、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、加熱槽内の温度制御は温度センサの検出値に基づ
いてON・OFF等の制御がなされるが、加熱槽に投入
される生ゴミ量は投入の度に変わるため、乾燥の終了時
間が処理毎に相違するため、タイマ等で終了時間を設定
することはできない。
When the garbage is automatically controlled by this garbage processing apparatus to finally dry the garbage to a smooth state or a smooth but somewhat oily state, the temperature control in the heating tank is not performed. Control such as ON / OFF is performed based on the detection value of the temperature sensor. However, since the amount of garbage put into the heating tank changes every time it is put in, the end time of drying differs for each processing. The end time cannot be set with.

【0004】そこで、加熱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、終了時間を検知するようにしていた。
[0004] Therefore, a temperature sensor is provided in the circulation path from the heating tank to the condenser, and the end time is detected by the temperature of the steam passing through the circulation path.

【0005】この生ゴミから発生する蒸気温度は、乾燥
中は略100℃であり、その後生ゴミ中の水分がなくな
るにつれて温度が低下するため、70℃まで低下したな
らば乾燥処理の終了としていた。
The temperature of the steam generated from the garbage is approximately 100 ° C. during drying, and then the temperature decreases as the moisture in the garbage disappears. Therefore, when the temperature drops to 70 ° C., the drying process is terminated. .

【0006】しかしながら、70℃に設定しても、周囲
温度により、特に夏季と冬季では温度差により、循環路
内の蒸気温度が影響され、設定の70℃に設定しても、
乾燥が十分でなく、生乾きやべた付いた状態となってし
まったり、過度に乾燥したり等する問題がある。また温
度の影響がなくても、生ゴミのゴミ質でも乾燥時間に相
違があるため、蒸気温度の設定温度だけで乾燥終了時間
を決定するには問題が多い。
However, even if the temperature is set to 70 ° C., the steam temperature in the circulation path is affected by the ambient temperature, particularly, the temperature difference between summer and winter, so that even if the temperature is set to 70 ° C.
There is a problem that drying is not sufficient, and it becomes dry, sticky, or excessively dried. Even if the temperature is not affected, there is a difference in the drying time even in the garbage of garbage, so that there are many problems in determining the drying end time only by the set temperature of the steam temperature.

【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、生ゴミの乾燥・固
化終了時間を確実に設定できる生ゴミ処理装置の自動運
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 provide an automatic operation control device for a garbage disposal apparatus capable of reliably setting a garbage drying / solidification end time. To provide.

【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、生ゴミを加熱して乾燥させる加熱槽
と、該加熱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装置において、上記コン
デンサに至る循環路に設けられた温度センサと、加熱槽
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100℃の一定温度から急激に降下するまでの蒸
発乾燥時間をカウントし、その蒸発乾燥時間に応じて、
乾燥終了時間を決定すると共に加熱槽の運転を停止する
を運転制御手段とを備えた生ゴミ処理装置の自動運転制
御装置である。
In order to solve the above-mentioned problems,
The invention according to claim 1 is provided with a heating tank for heating and drying garbage, a circulation path having a blower for sucking and circulating atmospheric gas in the heating tank, and a circulation path provided upstream of the blower in the circulation path. A garbage disposal comprising: a condenser for cooling the atmospheric gas to condense 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. In the apparatus, a temperature sensor provided in a circulation path leading to the condenser, a temperature of the temperature sensor is detected from the start of operation of the heating tank, and an operation time is integrated. Count the evaporative drying time from the constant temperature of ℃ until it suddenly drops, and according to the evaporative drying time,
An automatic operation control device for a garbage disposal device, comprising: an operation control means for determining a drying end time and stopping the operation of the heating tank.

【0009】請求項2の発明は、運転制御手段は、カウ
ントした蒸発乾燥時間をAとしたとき、その蒸発乾燥時
間Aから運転終了までの固形化時間をBとしたとき、そ
の固形化時間Bを、 B=k1A+k2 (時間) (但し、k1=0.1〜0.3,k2=0〜2.0) として終了時間を決定する請求項1記載の生ゴミ処理装
置の自動運転制御装置である。
According to a second aspect of the present invention, the operation control means determines that the counted evaporative drying time is A, the solidification time from the evaporative drying time A to the end of the operation is B, and the solidification time B is B = k1A + k2 (time) (where k1 = 0.1 to 0.3, k2 = 0 to 2.0) and the end time is determined. is there.

【0010】請求項3の発明は、運転制御手段は、加熱
槽内の内壁温度を120〜130℃、好ましくは125
℃に温度制御する請求項1又は2記載の生ゴミ処理装置
の自動運転制御装置である。
According to a third aspect of the present invention, the operation control means controls the inner wall temperature in the heating tank to 120 to 130 ° C., preferably 125 to 130 ° C.
3. The automatic operation control device for a garbage disposal device according to claim 1, wherein the temperature is controlled to a degree.

【0011】上記構成によれば、コンデンサに至る生ゴ
ミから発生する蒸気の温度を検出し、その温度が急激に
下がるときの時間を検出し、運転開始からその時間まで
の蒸発乾燥時間を検出することで、生ゴミ投入量や周囲
温度に影響されずに終了時間を決定できる。
According to the above configuration, the temperature of the steam generated from the garbage reaching the condenser is detected, the time when the temperature drops rapidly is detected, and the evaporative drying time from the start of operation to the time is detected. Thus, the end time can be determined without being affected by the amount of garbage input or the ambient temperature.

【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によって、本発明に係る生ゴミ乾燥処
理装置の全体の構成を説明する。
Referring to FIG. 1, the overall configuration of the garbage drying apparatus according to the present invention will be described.

【0014】図示するように、上記生ゴミ乾燥処理装置
1は、生ゴミRを加熱して乾燥させる加熱槽2と、加熱
槽2の内部の雰囲気ガスGを吸引して循環させて再度加
熱槽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Gを
冷却して雰囲気ガス内G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 the drawing, the garbage drying treatment apparatus 1 comprises a heating tank 2 for heating and drying the garbage R, and a suction tank for circulating and circulating an atmosphere gas G inside the heating tub 2 to reheat the garbage. And a circulation path 4 having a blower 3 for returning into the inside 2.
A condenser 5 for cooling the atmosphere gas G and condensing the vapor of the atmosphere gas G is connected to the upstream side of the blower 3 in the circulation path 4, and a condenser 5 is provided between the condenser 5 and the blower 3.
A gas-liquid separation tank 6 for separating gas and condensate from each other by gravity is provided.

【0015】加熱槽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加熱槽2内を密閉状態に
保つようになっている。
The heating 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 heating tank 2 in a sealed state.

【0016】撹拌部材9は、加熱槽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(こ
こでは三枚)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 heating vessel 2 and a plurality of rotating members 12 (here, radially attached to the rotating shaft 12 at equal intervals in the circumferential and axial directions). And three blades 14. The stirring member 9 is provided with a motor 15 for rotating the stirring member 9, and is connected to the rotating shaft 12 via a speed reducer 16.

【0017】加熱槽2の上部には、その内部の雰囲気ガ
スG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 G inside the heating tank 2 is formed in the upper part of the heating tank 2, and a suction pipe 25 forming a part of the circulation path 4 is connected to the opening 17. Have been.

【0018】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G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 G in the condenser 5. Is provided.

【0019】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G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 G cooled by the condenser 5 flows is formed in the upper part of the side surface, and the gas inlet 22 is formed in the upper part. 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.

【0020】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、加熱槽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 which 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 heating tank 2 and serving as a gas inlet. Have been.

【0021】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26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, 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 and the other end is opened 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 pressure H in the circulation passage 26 Pressure is compensated.

【0022】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 in the cold season.

【0023】この生ゴミ処理装置での生ゴミ処理は、生
ゴミを水切りを行って加熱槽2に投入し、加熱コイル8
で加熱し、同時にブロワ3で加熱槽2内の雰囲気ガスG
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G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より再度加熱槽2内に戻される。
In the garbage disposal in this garbage disposal apparatus, the garbage is drained, put into the heating tank 2 and heated by the heating coil 8.
And at the same time, the atmosphere gas G in the heating tank 2 by the blower 3
Is dried while circulating in a circulation path. The steam generated from the garbage is cooled and condensed by the condenser 5 together with the atmosphere gas G, the liquid component is removed in the gas-liquid separation tank 6, and the gas component is returned to the heating tank 2 through the inflow pipe 26.

【0024】加熱槽2内では攪拌部材9で攪拌されて粉
砕されながら徐々に水分が蒸発されてて乾燥・固化され
る。乾燥の結果残った固形物は、加熱槽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 heating tank 2, the water is gradually evaporated while being stirred and crushed by the stirring member 9 to be dried and solidified. Solid matter remaining as a result of drying is taken out from an outlet 34 formed in the heating tank 2 and buried in the soil to be recycled as a raw material for fertilizer, or incinerated together with general waste. .

【0025】さて、本発明においては、加熱槽2の容器
7の壁面温度を検出する温度センサ35が設けられ、ま
た加熱槽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、加熱槽2からの雰囲気ガス温度(蒸気温
度)を検出する温度センサ36が設けられ、これら温度
センサ35,36の検出値が運転制御手段40に入力さ
れる。
In the present invention, a temperature sensor 35 for detecting the wall surface temperature of the container 7 of the heating tank 2 is provided, and the suction pipe 25 forming the circulation path 4 between the heating tank 2 and the condenser 5 is provided with: A temperature sensor 36 for detecting the temperature (steam temperature) of the atmosphere gas from the heating tank 2 is provided, and the detection values of these temperature sensors 35 and 36 are input to the operation control means 40.

【0026】運転制御手段40は、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、温度センサ35の検
出値に応じて加熱コイル8をON・OFF制御して加熱
槽2内の温度を120〜130℃の適宜の温度、好まし
くは125℃に維持すると共に加熱槽2の運転開始から
時間を積算しながら吸引管25の温度センサ36からの
蒸気温度の変化の履歴をチェックし、運転開始から温度
センサ36の検出温度(蒸気温度)が、約100℃の一
定温度から急激に降下するまでの蒸発乾燥時間をカウン
トし、その蒸発乾燥時間に応じて、乾燥終了時間を決定
すると共に加熱槽2の運転を停止するようになってい
る。
The operation control means 40 activates the blower 3, the motor 15, and the cooling fan 21 at the start of operation, and simultaneously supplies electricity to the heating coil 8, and during the operation, the heating coil 8 according to the detection value of the temperature sensor 35. Is controlled to ON / OFF to maintain the temperature in the heating tank 2 at an appropriate temperature of 120 to 130 ° C., preferably 125 ° C., and the temperature sensor 36 of the suction pipe 25 while integrating the time from the start of the operation of the heating tank 2. Check the history of changes in steam temperature from the start, count the evaporative drying time from the start of operation until the temperature detected by the temperature sensor 36 (steam temperature) drops sharply from a constant temperature of about 100 ° C. The drying end time is determined according to the time, and the operation of the heating tank 2 is stopped.

【0027】この運転制御手段40の自動運転を図2に
より説明する。
The automatic operation of the operation control means 40 will be described with reference to FIG.

【0028】図2は、生ゴミ処理装置1で、食堂やレス
トランから出る一般の生ゴミR(約50kg,含水分約
80%)を乾燥(容器内温度を120℃に保持)したと
きの温度センサ36で検出した蒸気温度の経時変化を示
したものである。
FIG. 2 shows the temperature when the ordinary garbage R (about 50 kg, water content about 80%) coming out of a cafeteria or restaurant is dried (the temperature in the container is kept at 120 ° C.) in the garbage disposal apparatus 1. This shows a change with time of the steam temperature detected by the sensor 36.

【0029】先ず、蒸気温度は、40分程度で100℃
となり、それから約2時間程度100℃のままシチュー
状(或いはスープ状)となっており、この状態で水蒸気
が略一定の割合で発生し、その後、水分がなくなると生
ゴミが固体化し始め、生ゴミに結びついた(例えば食物
繊維中の)水分が徐々に蒸発するようになる。この水分
がなくなる時期には蒸気温度は100℃から急激に降下
し、80℃以下となったならば70℃まで漸次温度が下
がる温度変化となる。
First, the steam temperature is set to 100 ° C. for about 40 minutes.
Then, it is in a stew state (or soup state) at about 100 ° C. for about 2 hours. In this state, steam is generated at a substantially constant rate. Moisture associated with the garbage (eg, in dietary fiber) will gradually evaporate. When the moisture disappears, the steam temperature drops sharply from 100 ° C., and if it becomes 80 ° C. or less, the temperature changes gradually to 70 ° C.

【0030】そこで運転開始から蒸気温度が100℃か
ら急激に下がる時期T(例えば90℃になったとき)迄
を蒸発乾燥時間Aとし、その急激に下がる時期Tから終
了までの時間を固形化時間Bとしたとき、処理時間は、 処理時間=A+B とあらわせる。
Therefore, from the start of the operation to the time T when the steam temperature suddenly drops from 100 ° C. (for example, when the temperature reaches 90 ° C.) is referred to as the evaporative drying time A. When B is set, the processing time is expressed as follows: processing time = A + B.

【0031】図3は、横軸を90℃を切るまでの時間
(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. 3 shows the data when the solidification time B is arbitrarily selected with respect to the time until the horizontal axis falls below 90 ° C. (evaporation drying time A), and the drying treatment is performed. It shows that the product was dry and solidified in a smooth and dry state, or in a slightly oily state, and the mark ■ indicates that the solidification was insufficient and it was sticky or muddy and the drying and solidification was insufficient. Is shown.

【0032】図3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. 3, 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.

【0033】また、図4は、加熱槽2に投入した生ゴミ
量と最適な処理時間(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
ろ処理量と処理時間に比例関係があることが認められ
た。
FIG. 4 shows the relationship between the amount of garbage charged into the heating tank 2 and the optimum processing time (A + B).
When variously changed to garbage of 20 to 60 kg and dried and solidified, it was recognized that there was a proportional relationship between the processing amount and the processing time.

【0034】そこで、この蒸発乾燥AからBを図3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. 3, 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).

【0035】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、標準的の生ゴミであり、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.

【0036】従って、上記式を B=k1A+k2 (時間) 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40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 to B = k1A + k2 (time), and the operation control means 40 can change the coefficient according to the dust type so that the coefficients k1 and k2 can be changed according to the dust type.

【0037】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
適な処理時間(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 changing k2 in the range of 0 to 2.0 and k2 in the range of 0 to 2.0, it is possible to set the optimal processing time (A + B) for drying and solidification according to the type of all garbage. It becomes possible.

【0038】以上のように、本発明においては、100
℃から急激に蒸気温度の下がる時期(例えば90℃)を
運転制御手段40が、吸気管25に温度センサ36の検
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)となったときに加熱槽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, 100
The operation control means 40 obtains a time (for example, 90 ° C.) at which the steam temperature suddenly drops from the temperature from the temperature detected by the temperature sensor 36 to the intake pipe 25 and counts the time from the start of the operation to the time to evaporate the drying time A The remaining solidification time B is calculated from the obtained evaporative drying time A, and when A + B (time) has elapsed from the start of the processing, the energization of the heating coil 8 in the heating tank 2 is stopped to perform the processing. Terminate.

【0039】このように蒸発乾燥時間Aから処理時間を
決定することで、乾燥・固化が常に良好な状態で自動運
転することが可能となる。
By determining the processing time from the evaporative drying time A in this manner, the automatic operation can be performed in a state where the drying and solidification are always good.

【0040】[0040]

【発明の効果】以上要するに本発明によれば、コンデン
サに至る生ゴミから発生する蒸気の温度を検出し、その
温度が急激に下がるときの時間を検出し、運転開始から
その時間までの蒸発乾燥時間を検出することで、生ゴミ
投入量や周囲温度に影響されずに終了時間を決定できる
という優れた効果を発揮する。
In summary, according to the present invention, the temperature of the steam generated from the garbage reaching the condenser is detected, the time when the temperature drops rapidly is detected, and the evaporative drying from the start of operation to the time is detected. By detecting the time, an excellent effect that the end time can be determined without being influenced by the amount of raw garbage or the ambient temperature is exhibited.

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

【図1】本発明に係る生ゴミ乾燥処理装置の実施の形態
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 drying processing apparatus according to the present invention.

【図2】本発明において、コンデンサに至る蒸気温度の
経時変化を示す図である。
FIG. 2 is a diagram showing a change over time of a steam temperature reaching a condenser in the present invention.

【図3】本発明において、蒸発乾燥時間Aと固形化時間
Bの関係を示す図である。
FIG. 3 is a diagram showing a relationship between an evaporation drying time A and a solidification time B in the present invention.

【図4】本発明において、生ゴミ処理量と処理時間の関
係を示すずである。
FIG. 4 is a diagram illustrating a relationship between a raw garbage processing amount and a processing time in the present invention.

【符号の説明】[Explanation of symbols]

1 生ゴミ乾燥処理装置 2 加熱槽 3 ブロワ 4 循環路 5 コンデンサ 6 気液分離槽 8 加熱コイル 35 温度センサ 36 温度センサ 40 運転制御手段 DESCRIPTION OF SYMBOLS 1 Garbage drying apparatus 2 Heating tank 3 Blower 4 Circulation path 5 Condenser 6 Gas-liquid separation tank 8 Heating coil 35 Temperature sensor 36 Temperature sensor 40 Operation control means

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) F26B 21/00 F26B 23/06 A 23/06 B09B 3/00 ZABZ Fターム(参考) 3L113 AA04 AB05 AC08 AC21 AC45 AC46 AC58 AC67 BA01 CA08 CA20 CB05 DA30 4D004 AA03 AC01 CA12 CA15 CA22 CA42 CA48 CB04 CB27 CB31 CB32 CB44 DA01 DA02 DA03 DA06 DA20 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) F26B 21/00 F26B 23/06 A 23/06 B09B 3/00 ZABZ F-term (Reference) 3L113 AA04 AB05 AC08 AC21 AC45 AC46 AC58 AC67 BA01 CA08 CA20 CB05 DA30 4D004 AA03 AC01 CA12 CA15 CA22 CA42 CA48 CB04 CB27 CB31 CB32 CB44 DA01 DA02 DA03 DA06 DA20

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 生ゴミを加熱して乾燥させる加熱槽と、
該加熱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装置において、上記コンデン
サに至る循環路に設けられた温度センサと、加熱槽の運
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100℃の一定温度から急激に降下するまでの蒸発乾
燥時間をカウントし、その蒸発乾燥時間に応じて、乾燥
終了時間を決定すると共に加熱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装置の
自動運転制御装置。
1. A heating tank for heating and drying garbage,
A circulation path having a blower that sucks and circulates the atmosphere gas in the heating tank, and a condenser that is provided upstream of the blower in the circulation path and cools the atmosphere gas to condense vapor in the atmosphere gas; In a garbage disposal apparatus provided with a gas-liquid separation tank provided between the condenser and the blower for gravity-separating a gas and a condensed liquid, a temperature sensor provided in a circulation path leading to the condenser, From the start of operation, the temperature of the temperature sensor is detected and the operation time is integrated.
Operation control means for counting the evaporative drying time from a constant temperature of about 100 ° C. until the temperature suddenly drops, determining the drying end time according to the evaporative drying time, and stopping the operation of the heating tank. An automatic operation control device for a garbage disposal device.
【請求項2】 運転制御手段は、カウントした蒸発乾燥
時間をAとしたとき、その蒸発乾燥時間Aから運転終了
までの固形化時間をBとしたとき、その固形化時間B
を、 B=k1A+k2 (時間) (但し、k1=0.1〜0.3,k2=0〜2.0) として終了時間を決定する請求項1記載の生ゴミ処理装
置の自動運転制御装置。
2. The operation control means, when the counted evaporative drying time is A, and when the solidifying time from the evaporating drying time A to the end of the operation is B, the solidifying time B
B = k1A + k2 (time) (where k1 = 0.1 to 0.3, k2 = 0 to 2.0) and the end time is determined.
【請求項3】 運転制御手段は、加熱槽内の内壁温度を
120〜130℃、好ましくは125℃に温度制御する
請求項1又は2記載の生ゴミ処理装置の自動運転制御装
置。
3. The automatic operation control apparatus for a garbage disposal apparatus according to claim 1, wherein the operation control means controls the temperature of the inner wall in the heating tank to 120 to 130 ° C., preferably 125 ° C.
JP10370561A 1998-12-25 1998-12-25 Automatic operation controller for garbage disposal system Pending JP2000189925A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP10370561A JP2000189925A (en) 1998-12-25 1998-12-25 Automatic operation controller for garbage disposal system
KR1019990044332A KR20000047528A (en) 1998-12-25 1999-10-13 Garbage Processing Machine And Method Of Automatically Controlling The Same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10370561A JP2000189925A (en) 1998-12-25 1998-12-25 Automatic operation controller for garbage disposal system

Publications (1)

Publication Number Publication Date
JP2000189925A true JP2000189925A (en) 2000-07-11

Family

ID=18497224

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10370561A Pending JP2000189925A (en) 1998-12-25 1998-12-25 Automatic operation controller for garbage disposal system

Country Status (1)

Country Link
JP (1) JP2000189925A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005230628A (en) * 2004-02-17 2005-09-02 Takagi Ind Co Ltd Method and apparatus for treating garbage
JP2007185659A (en) * 2007-03-22 2007-07-26 Tokyo Gas Co Ltd Garbage disposal method and garbage disposal apparatus
CN101818986A (en) * 2010-04-23 2010-09-01 中国科学院广州能源研究所 Heat-accumulating solar energy and heat pump combined drying device capable of realizing multi-mode operation
CN111536767A (en) * 2020-05-08 2020-08-14 潍坊学院 Integrative device of drying cooling of preparation cladding type nickel cobalt lithium manganate cathode material
KR102598019B1 (en) * 2023-04-03 2023-11-03 주식회사 명지미래솔루션 A food waste disposal device and method controlling thereof

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005230628A (en) * 2004-02-17 2005-09-02 Takagi Ind Co Ltd Method and apparatus for treating garbage
JP2007185659A (en) * 2007-03-22 2007-07-26 Tokyo Gas Co Ltd Garbage disposal method and garbage disposal apparatus
CN101818986A (en) * 2010-04-23 2010-09-01 中国科学院广州能源研究所 Heat-accumulating solar energy and heat pump combined drying device capable of realizing multi-mode operation
CN111536767A (en) * 2020-05-08 2020-08-14 潍坊学院 Integrative device of drying cooling of preparation cladding type nickel cobalt lithium manganate cathode material
CN111536767B (en) * 2020-05-08 2021-06-04 潍坊学院 Integrative device of drying cooling of preparation cladding type nickel cobalt lithium manganate cathode material
KR102598019B1 (en) * 2023-04-03 2023-11-03 주식회사 명지미래솔루션 A food waste disposal device and method controlling thereof

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