JP2005066449A - Garbage treating method and apparatus therefor - Google Patents

Garbage treating method and apparatus therefor Download PDF

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JP2005066449A
JP2005066449A JP2003298868A JP2003298868A JP2005066449A JP 2005066449 A JP2005066449 A JP 2005066449A JP 2003298868 A JP2003298868 A JP 2003298868A JP 2003298868 A JP2003298868 A JP 2003298868A JP 2005066449 A JP2005066449 A JP 2005066449A
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temperature
heating
garbage
steam
outlet side
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JP4255336B2 (en
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Hiroaki Yoshikawa
博明 吉川
Hiroki Yoshimura
洋城 吉村
Eiji Takahashi
英二 高橋
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Takagi Industrial Co Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

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Abstract

<P>PROBLEM TO BE SOLVED: To provide a garbage treating method and an apparatus therefor by which completion of garbage drying and finish of garbage heating treatment can be made to coincide. <P>SOLUTION: Heating temperature by a heating means (a heater 32) in a treating tank 4 is set to a maximum heating temperature at an initial stage and to a minimum heating temperature at an final stage. The garbage 3 is heated by changing the heating temperature within the temperature range. Steam 40 generated in the treating tank by this heating treatment is made to pass a condensing means (a radiator 42) to separate condensed water 58 and the steam from which the condensed water is separated is circulated to the treating tank and temperature of the steam at an inlet side of the condensing means and temperature of the steam at an outlet side thereof are detected. In the case of heating at the minimum heating temperature, when temperature difference between the inlet side temperature and the outlet side temperature exceeds reference temperature value, the heating treatment is finished. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、生ごみを加熱して乾燥させる生ごみ処理に関し、乾燥終了の適正化を実現した生ごみ処理方法及びその装置に関する。
The present invention relates to a garbage treatment for heating and drying garbage, and relates to a garbage treatment method and apparatus for realizing the completion of drying.

厨房等から出る生ごみは多量の水分、油、繊維等を多く含んでおり、これらを乾燥により除去すれば、減量化を図ることができる。乾燥させた生ごみは、有機肥料原料としての用途の他、廃棄処理が容易になる。この生ごみ乾燥処理に関する先行特許文献には次のようなものがある。
特開2002−355635号公報 この特許文献1には、生ごみを加熱する処理槽から出る蒸気を凝縮手段に循環させて冷却させると、蒸気から凝縮水が分離するが、この凝縮水を分離させた蒸気を処理槽に戻す生ごみ処理方法及びその装置が開示されている。この処理方法及び装置では、処理槽内の生ごみの温度を所定温度に到達させたとき、生ごみに加える熱量を減少させるとともに、凝縮手段の入側温度と出側温度との温度差により加熱制御を行っている。
Garbage from kitchens contains a large amount of water, oil, fiber, etc., and if these are removed by drying, the amount can be reduced. The dried garbage can be easily disposed of as well as used as an organic fertilizer raw material. Prior patent documents relating to this garbage drying treatment include the following.
JP, 2002-355635, A In this patent document 1, when steam which circulates from a processing tub which heats garbage is circulated to a condensation means and it is made to cool, condensed water will separate from steam, but this condensed water is separated. A garbage disposal method and apparatus for returning the steam to the treatment tank are disclosed. In this treatment method and apparatus, when the temperature of the garbage in the treatment tank reaches a predetermined temperature, the amount of heat applied to the garbage is reduced, and heating is performed by the temperature difference between the inlet side temperature and the outlet side temperature of the condensing means. Control is in progress.

ところで、生ごみは油分や水分に多少の違い等の質的な相違があり、その乾燥処理の結果はその質や量の他、外的条件である外気温の高低によって異なるものである。そこで、外気温度と、乾燥途上で発生する蒸気を冷却して凝縮水を蒸気から分離するラジエターの入側温度及び出側温度とを参照して生ごみの乾燥終了を判断する場合、生ごみによっては乾燥が進みすぎて肥料としては不適、乾燥が不十分なため再乾燥が必要である等、乾燥度がまちまちになるという不都合がある。この場合、外気温を検出するセンサが必要であり、外気温情報を制御に用いるという不都合もある。このような課題は、特許文献1には開示されておらず、その解決手段も提示されていない。   By the way, raw garbage has qualitative differences such as some differences in oil content and moisture, and the result of the drying treatment differs depending on the external temperature, which is an external condition, in addition to the quality and quantity. Therefore, when judging the end of drying of garbage by referring to the outside air temperature and the inlet side temperature and outlet side temperature of the radiator that cools the steam generated during drying and separates condensed water from the steam, However, there is a disadvantage that the degree of dryness varies, for example, it is unsuitable as a fertilizer due to excessive drying and re-drying is necessary because of insufficient drying. In this case, a sensor for detecting the outside air temperature is necessary, and there is a disadvantage that the outside air temperature information is used for control. Such a problem is not disclosed in Patent Document 1 and no solution is presented.

そこで、本発明は、斯かる課題を解決することを目的とし、生ごみの乾燥完了で乾燥処理を終了させることができる生ごみ処理方法及びその装置を提供することを目的とする。   Accordingly, an object of the present invention is to provide a garbage disposal method and apparatus capable of ending the drying process upon completion of drying of garbage.

上記目的を達成するため、本発明の生ごみ処理方法は、処理槽4で加熱手段(ヒータ32)により加熱温度を初期段階で最高加熱温度、最終段階で最低加熱温度とし、その温度幅内で前記加熱温度を可変させて生ごみ3を加熱する処理と、この加熱処理により前記処理槽で発生する蒸気40を凝縮手段(ラジエター42)を通して凝縮水58を分離するとともに、凝縮水が分離された蒸気を前記処理槽に循環させる処理と、前記凝縮手段の前記蒸気の入側温度と出側温度とを検出する処理と、前記最低加熱温度で加熱する場合に前記入側温度と前記出側温度との差温が基準温度を超えたとき、前記加熱処理を終了させる処理とを含む構成である。   In order to achieve the above object, the garbage processing method of the present invention is configured such that the heating temperature in the treatment tank 4 is set to the highest heating temperature in the initial stage and the lowest heating temperature in the final stage by the heating means (heater 32). The process of heating the garbage 3 by changing the heating temperature, and the condensed water 58 was separated from the steam 40 generated in the treatment tank by the heat treatment through the condensing means (radiator 42), and the condensed water was separated. A process of circulating the steam to the treatment tank, a process of detecting the inlet side temperature and the outlet side temperature of the steam of the condensing means, and the inlet side temperature and the outlet side temperature when heating at the minimum heating temperature And a process of terminating the heat treatment when the temperature difference with the reference temperature exceeds a reference temperature.

この生ごみ処理方法においては、処理槽に入れた生ごみを加熱手段により加熱しており、加熱手段の形態は電熱、燃焼熱等何れのものでもよい。生ごみの加熱温度には、最高加熱温度と最低加熱温度とを設定し、これらの温度幅内で変更される。このような加熱温度の設定及び変更により、処理槽内で生ごみは焦げ付きを生じることなく、その乾燥が行われる。   In this garbage disposal method, the garbage put in the treatment tank is heated by a heating means, and the heating means may be in any form such as electric heat or combustion heat. The maximum heating temperature and the minimum heating temperature are set as the heating temperature of the garbage, and are changed within these temperature ranges. By such setting and changing of the heating temperature, the garbage is dried in the treatment tank without causing burning.

そして、生ごみの乾燥処理で処理槽から発生した蒸気は、凝縮手段に導かれて凝縮水と分離された後、処理槽に戻される。凝縮手段で発生する凝縮水は凝縮手段による冷却に依存し、これはその入側温度と出側温度とに現れる。   And the vapor | steam which generate | occur | produced from the processing tank by the drying process of garbage is guided to a condensation means, and is returned to a processing tank, after being isolate | separated from condensed water. The condensed water generated in the condensing means depends on the cooling by the condensing means, which appears at the inlet side temperature and the outlet side temperature.

そこで、凝縮手段の入側温度と出側温度との差温について、乾燥完了が想定される基準温度が設定され、入側温度と出側温度との差温がこの基準温度を超えたとき、加熱処理を終了すれば、安定した乾燥状態を得ることができる。即ち、凝縮手段の入側温度と出側温度の変化の影響を受けることなく、夏と冬、昼と夜というような外気温の相違を吸収でき、しかも、凝縮手段の効率の変化やばらつきにも対応し、含水率のばらつきのない処理物が得られる。   Therefore, for the temperature difference between the inlet side temperature and the outlet side temperature of the condensing means, a reference temperature that is assumed to be dry is set, and when the difference temperature between the inlet side temperature and the outlet side temperature exceeds this reference temperature, When the heat treatment is completed, a stable dry state can be obtained. In other words, it is possible to absorb the difference in outside air temperature such as summer and winter, day and night without being affected by changes in the inlet side temperature and outlet side temperature of the condensing means, and to the change and variation in efficiency of the condensing means. Can be obtained, and a treated product having no variation in moisture content can be obtained.

上記目的を達成するためには、前記基準温度は、前記最低加熱温度に移行する前段階の加熱温度下で検出される前記入側温度と前記出側温度との最大差温又はこの最大差温に所定値を加えた値に構成してもよい。斯かる構成とすれば、生ごみの未乾燥を防止でき、乾燥度の均一性が高められる。   In order to achieve the above object, the reference temperature is the maximum temperature difference between the inlet side temperature and the outlet side temperature detected under the heating temperature before the transition to the minimum heating temperature, or the maximum temperature difference. A predetermined value may be added to the value. With such a configuration, it is possible to prevent undried food waste and to improve the uniformity of the dryness.

上記目的を達成するため、本発明の生ごみ処理装置は、加熱手段(ヒータ32)を備え、装填された生ごみ3に加熱処理を施す処理槽4と、この処理槽で前記生ごみから発生する蒸気40から凝縮水58を分離する凝縮手段(ラジエター42)と、この凝縮手段と前記処理槽との間に連結されて前記蒸気を前記凝縮手段に循環させる循環手段(循環路44)と、前記凝縮手段の前記蒸気の入側温度と出側温度とを検出する温度検出手段(温度センサ66、68)と、前記処理槽で前記加熱手段により加熱温度を初期段階で最高加熱温度、最終段階で最低加熱温度とし、その温度幅内で前記加熱温度を可変させて前記生ごみを加熱するとともに、前記最低加熱温度に移行する前の加熱温度下で前記入側温度と前記出側温度との差温に基準温度を設定し、前記最低加熱温度で加熱する場合に前記入側温度と前記出側温度との差温が前記基準温度を超えたとき、前記加熱処理を終了させる制御手段(制御装置86)とを含む構成である。   In order to achieve the above object, the garbage processing apparatus of the present invention is provided with a heating means (heater 32), and a treatment tank 4 that heats the loaded garbage 3 and generated from the garbage in this treatment tank. A condensing means (radiator 42) for separating condensed water 58 from the steam 40, and a circulating means (circulation path 44) connected between the condensing means and the treatment tank for circulating the steam to the condensing means; Temperature detecting means (temperature sensors 66 and 68) for detecting the inlet side temperature and the outlet side temperature of the steam of the condensing means, and the heating temperature in the treatment tank by the heating means in the initial stage, the highest heating temperature, and the final stage And the heating temperature is varied within the temperature range to heat the garbage, and the entry side temperature and the exit side temperature under the heating temperature before shifting to the minimum heating temperature. Set the reference temperature to the differential temperature And a control means (control device 86) for terminating the heat treatment when the difference between the inlet side temperature and the outlet side temperature exceeds the reference temperature when heating at the minimum heating temperature. It is a configuration.

斯かる構成において、処理槽は、加熱手段を備え、装填された生ごみに加熱処理を施す容器である。凝縮手段では、この処理槽で生ごみから発生する蒸気から凝縮水が分離される。循環手段は、この凝縮手段と処理槽との間に連結されており、処理槽に発生した蒸気を凝縮手段に循環させる。また、温度検出手段には、乾燥処理の完了情報として凝縮手段の蒸気の入側温度と出側温度とを検出する。そして、制御手段は、処理槽で加熱手段により加熱温度を初期段階で最高加熱温度、最終段階で最低加熱温度とし、その温度幅内で加熱温度を可変させて生ごみを加熱するとともに、最低加熱温度に移行する前の加熱温度下で入側温度と出側温度との差温に基準温度を設定し、最低加熱温度で加熱する場合に入側温度と出側温度との差温が基準温度を超えたとき、加熱処理を終了させる。   In such a configuration, the treatment tank is a container that includes heating means and heats the loaded garbage. In the condensing means, condensed water is separated from the steam generated from the garbage in this treatment tank. The circulation means is connected between the condensing means and the treatment tank, and circulates the steam generated in the treatment tank to the condensation means. Further, the temperature detecting means detects the vapor inlet side temperature and the outlet side temperature of the condensing means as the drying process completion information. Then, the control means sets the heating temperature by the heating means in the treatment tank to the maximum heating temperature in the initial stage and the minimum heating temperature in the final stage, varies the heating temperature within the temperature range, heats the garbage, and also sets the minimum heating temperature. When the reference temperature is set to the difference temperature between the inlet side temperature and the outlet side temperature under the heating temperature before shifting to the temperature, and the heating is performed at the minimum heating temperature, the difference temperature between the inlet side temperature and the outlet side temperature is the reference temperature. When the value exceeds, the heat treatment is terminated.

斯かる構成によれば、既述の生ごみ処理方法が実現され、安定した乾燥状態を得ることができる。この結果、凝縮手段の入側温度と出側温度の変化の影響を受けることなく、夏と冬、昼と夜というような外気温の相違が吸収され、しかも、凝縮手段の効率の変化やばらつきにも対応し、含水率にばらつきのない処理物が得られる。
According to such a configuration, the above-described garbage disposal method is realized, and a stable dry state can be obtained. As a result, differences in outside air temperature such as summer and winter, day and night are absorbed without being affected by changes in the inlet side temperature and outlet side temperature of the condensing means, and changes and variations in the efficiency of the condensing means are absorbed. In addition, a processed product with no variation in moisture content can be obtained.

(1) 本発明によれば、生ごみの質や処理量に関係なく、また、外気温の高低に関係なく、乾燥完了とともに加熱処理を終了でき、均一な乾燥処理を実現することができる。   (1) According to the present invention, the heat treatment can be completed upon completion of drying regardless of the quality and amount of garbage and regardless of the outside air temperature, and a uniform drying treatment can be realized.

(2) また、本発明によれば、所望の含水率を持つ乾燥処理が可能になるので、焦げ付きのない肥料を生ごみから製造できるとともに、廃棄処理の容易化を図ることができる。
(2) Further, according to the present invention, it is possible to perform a drying process having a desired moisture content, so that it is possible to produce a non-burning fertilizer from garbage and facilitate the disposal process.

本発明の実施形態について、図1を参照して説明する。図1は、本発明の実施形態に係る生ごみ処理装置の概要を示している。   An embodiment of the present invention will be described with reference to FIG. FIG. 1 shows an outline of a garbage disposal apparatus according to an embodiment of the present invention.

この生ごみ処理装置2において、乾燥処理の被処理物として例えば、生ごみ3が収容される処理槽4には例えば、底面側を半円筒状とした容器が用いられ、この処理槽4内には生ごみ3を攪拌する攪拌手段としての攪拌羽根車であるスクレーパ6が設けられている。このスクレーパ6は、例えば、回転軸8に放射状に突設した複数のアーム10の先端に攪拌羽根12を取り付けたものであり、回転軸8の両端が処理槽4の側面に設けられた軸受14によって回転可能に支持されている。回転軸8には、攪拌モータ16からの回転力を受けるためのプーリ18が取り付けられ、このプーリ18と攪拌モータ16側の駆動プーリ20との間には、駆動チェーン22が懸け回されている。即ち、スクレーパ6には攪拌モータ16により矢印A、Bで示すように、所望の回転、連続回転、断続回転、正逆回転等の回転パターンを持つ回転が付与される。このスクレーパ6の回転により、処理槽4内の生ごみ3が攪拌されるとともに粉砕される。この実施形態では、スクレーパ6の回転駆動手段として攪拌モータ16を用いているが、エンジン等の駆動手段を用いてもよく、回転伝達手段にはプーリ18及び駆動プーリ20に代えてスプロケットホイール及びチェーンでもよく、また、ギア機構等を用いてもよい。   In this garbage processing apparatus 2, for example, a container having a semi-cylindrical bottom surface is used as the treatment tank 4 in which the garbage 3 is accommodated as an object to be dried. A scraper 6 which is a stirring impeller as stirring means for stirring the garbage 3 is provided. The scraper 6 is, for example, one in which stirring blades 12 are attached to the tips of a plurality of arms 10 projecting radially on the rotating shaft 8, and both ends of the rotating shaft 8 are provided on bearings 14 provided on the side surfaces of the processing tank 4. Is supported rotatably. A pulley 18 for receiving a rotational force from the stirring motor 16 is attached to the rotating shaft 8, and a drive chain 22 is suspended between the pulley 18 and the driving pulley 20 on the stirring motor 16 side. . That is, as shown by arrows A and B, the scraper 6 is provided with a rotation having a rotation pattern such as desired rotation, continuous rotation, intermittent rotation, and forward / reverse rotation, as indicated by arrows A and B. By the rotation of the scraper 6, the garbage 3 in the treatment tank 4 is stirred and pulverized. In this embodiment, the agitation motor 16 is used as the rotation driving means of the scraper 6. However, a driving means such as an engine may be used. Instead of the pulley 18 and the driving pulley 20, the sprocket wheel and the chain are used as the rotation transmission means. Alternatively, a gear mechanism or the like may be used.

この処理槽4の上部側には、生ごみ3を処理槽4内に装填するための投入口24が形成されているとともに、この投入口24を開閉する扉26がヒンジ28で開閉可能に取り付けられている。即ち、扉26は把手30を持って開閉可能であり、閉止状態では図示しないパッキン等の封止手段によって処理槽4を密封状態に維持するものである。   An inlet 24 for loading the garbage 3 into the processing tank 4 is formed on the upper side of the processing tank 4, and a door 26 for opening and closing the inlet 24 is attached by a hinge 28 so as to be opened and closed. It has been. That is, the door 26 can be opened and closed with the handle 30 and, in the closed state, the processing tank 4 is maintained in a sealed state by a sealing means such as packing (not shown).

また、この処理槽4の底面部には処理槽4内の生ごみ3の加熱手段としてヒータ32が設置されている。このヒータ32には、加熱温度として最高加熱温度、最低加熱温度とともにこれらの最高加熱温度と最低加熱温度との温度幅内に段階的又は連続的に変更させる加熱温度が設定される。ヒータ32の発熱温度の検出手段、即ち、第1の温度検出手段として温度センサ34が設置されている。この温度センサ34は、換言すれば、生ごみ3に加えられる熱量についての加熱温度を検出する温度検出手段を構成している。この実施形態にあっては、処理槽4の湾曲面に沿ってヒータ32が設置されている。加熱手段としては、石油や燃料ガスを燃焼させるバーナ等を用いてもよく、エンジン等を熱源として用いてもよい。また、処理槽4内の処理温度、槽壁温度等を検出する第2の温度検出手段として温度センサ36が処理槽4の例えば、側壁の外面部に取り付けられている。生ごみ3の処理温度が沸騰温度100℃を超えると、生ごみ3の焦げ付きが発生し易くなるので、その処理温度、槽壁温度が温度センサ36によって検出される。   A heater 32 is installed on the bottom surface of the treatment tank 4 as a heating means for the garbage 3 in the treatment tank 4. In the heater 32, a heating temperature that is changed stepwise or continuously within the temperature range between the maximum heating temperature and the minimum heating temperature is set as well as the maximum heating temperature and the minimum heating temperature. A temperature sensor 34 is installed as a means for detecting the heat generation temperature of the heater 32, that is, a first temperature detecting means. In other words, the temperature sensor 34 constitutes temperature detection means for detecting the heating temperature for the amount of heat applied to the garbage 3. In this embodiment, the heater 32 is installed along the curved surface of the processing tank 4. As the heating means, a burner or the like for burning oil or fuel gas may be used, and an engine or the like may be used as a heat source. Further, a temperature sensor 36 is attached to, for example, the outer surface of the side wall of the processing tank 4 as second temperature detection means for detecting the processing temperature in the processing tank 4, the tank wall temperature, and the like. When the treatment temperature of the garbage 3 exceeds the boiling temperature 100 ° C., the garbage 3 is easily burnt, and the treatment temperature and the tank wall temperature are detected by the temperature sensor 36.

そして、処理槽4で発生した蒸気40を冷却させて凝縮する冷却手段ないし凝縮手段としてラジエター42が設置され、このラジエター42と処理槽4との間には蒸気40を循環させるための循環手段として循環路44が設けられており、この循環路44は往管46及び戻管48で構成されている。即ち、処理槽4内で発生した蒸気40はラジエター42に流れ、冷却、凝縮させた後、処理槽4内に循環する。ラジエター42は、蒸気40を分流させて通流する複数の細管50を備えるとともにその細管50に放熱フィン52を取り付けたものである。このラジエター42には放熱手段として例えば、放熱ファン54が設けられ、この放熱ファン54は駆動手段であるモータ56によって駆動される。この放熱ファン54の回転によってラジエター42に冷却空気Cが通流して放熱が促進され、ラジエター42内を通過する蒸気40が放熱、冷却され、凝縮水58を生じる。   A radiator 42 is installed as a cooling means or a condensing means for cooling and condensing the steam 40 generated in the treatment tank 4. As a circulation means for circulating the steam 40 between the radiator 42 and the treatment tank 4. A circulation path 44 is provided, and the circulation path 44 includes an outward pipe 46 and a return pipe 48. That is, the steam 40 generated in the processing tank 4 flows to the radiator 42, is cooled and condensed, and then circulates in the processing tank 4. The radiator 42 includes a plurality of thin tubes 50 through which the steam 40 is divided and flows, and heat radiating fins 52 are attached to the thin tubes 50. The radiator 42 is provided with, for example, a heat radiating fan 54 as a heat radiating means, and the heat radiating fan 54 is driven by a motor 56 which is a driving means. The rotation of the heat dissipating fan 54 causes the cooling air C to flow through the radiator 42 to promote heat dissipation, and the steam 40 passing through the radiator 42 is dissipated and cooled to generate condensed water 58.

この実施形態では、ラジエター42は放熱面を水平方向にした縦置型であり、その底面側に設けられた気水分離部60に蒸気40の冷却により発生する凝縮水58が導かれる。この気水分離部60には排水管62が連結されており、この排水管62の中途部には外気を取り入れるための給気ホース64が設けられている。   In this embodiment, the radiator 42 is a vertical type in which the heat radiating surface is in the horizontal direction, and the condensed water 58 generated by the cooling of the steam 40 is guided to the steam-water separation unit 60 provided on the bottom surface side. A drain pipe 62 is connected to the air / water separator 60, and an air supply hose 64 for taking in outside air is provided in the middle of the drain pipe 62.

往管46が接続されているラジエター42の入側にはその入側温度を検出する第3の温度検出手段として、温度センサ66が設置され、また、その出側温度を検出する第4の温度検出手段として、温度センサ68が気水分離部60側に設けられている。また、戻管48には蒸気40を強制的に循環させる手段として循環ファン70が取り付けられ、この循環ファン70は駆動手段であるモータ72によって駆動される。この循環ファン70の下流側の戻管48には、循環ファン70により凝縮後の気体41に加えられる圧送圧力とともに気体41の一部を外気に導く排気手段として排気管74が分岐されている。この場合、循環ファン70側に導かれる凝縮後の気体41は、戻管48を通して処理槽4側に流れる気体41Aと排気管74側に流れる気体41Bとに分離される。排気管74には、触媒等を用いて臭気を分解する脱臭器76が設置され、この脱臭器76には脱臭反応を活性化させるため、触媒を加熱する手段としてヒータ78が設けられている。   A temperature sensor 66 is installed as a third temperature detecting means for detecting the inlet side temperature on the inlet side of the radiator 42 to which the outgoing pipe 46 is connected, and a fourth temperature for detecting the outlet side temperature is provided. As a detection means, a temperature sensor 68 is provided on the side of the steam / water separator 60. A circulation fan 70 is attached to the return pipe 48 as a means for forcibly circulating the steam 40, and the circulation fan 70 is driven by a motor 72 as a drive means. An exhaust pipe 74 is branched from the return pipe 48 on the downstream side of the circulation fan 70 as exhaust means for guiding a part of the gas 41 to the outside air together with the pressure applied to the gas 41 condensed by the circulation fan 70. In this case, the condensed gas 41 guided to the circulation fan 70 side is separated through the return pipe 48 into a gas 41A flowing to the processing tank 4 side and a gas 41B flowing to the exhaust pipe 74 side. The exhaust pipe 74 is provided with a deodorizer 76 that decomposes odors using a catalyst or the like, and the deodorizer 76 is provided with a heater 78 as means for heating the catalyst in order to activate the deodorization reaction.

なお、安定して気体41が排気管74に流れ、脱臭器76で脱臭できるようにするために、戻管48内にはふさぎ板90が設けられている。このふさぎ板90により戻管48内の内圧が高められる。排水管62中途部には外気を取り入れるための給気ホース64が設けられ、循環ファン70側に導かれる凝縮後の気体41の圧力の平均化が図られている。斯かる構造とすることにより、脱臭器76の小型化を図りながら、効率的な脱臭を行うことができる。   A blocking plate 90 is provided in the return pipe 48 so that the gas 41 stably flows into the exhaust pipe 74 and can be deodorized by the deodorizer 76. This blocking plate 90 increases the internal pressure in the return pipe 48. An air supply hose 64 for taking in outside air is provided in the middle of the drain pipe 62 to average the pressure of the condensed gas 41 guided to the circulation fan 70 side. By adopting such a structure, it is possible to perform efficient deodorization while reducing the size of the deodorizer 76.

次に、制御装置86について、図2を参照して説明する。図2は生ごみ処理装置の制御装置の概要を示している。   Next, the control device 86 will be described with reference to FIG. FIG. 2 shows an outline of the control device of the garbage disposal apparatus.

操作入力装置94からの運転指令、温度センサ34、36、66、68等の制御情報により攪拌モータ16の回転制御やヒータ32の駆動及び温度制御を行う制御手段として制御装置86が設けられている。この制御装置86は、例えば、中央演算処理装置(CPU)96、EEPROM97、RAM98、タイマ99が設けられ、また、操作入力装置94から運転を指令する運転指令等の入力や、温度センサ34、36、66、68等からの入力等を受ける入力部90、ヒータ32、攪拌モータ16、循環ファンモータ72、放熱ファンモータ56、脱臭ヒータ78等を制御するための出力を行う駆動出力部92が設けられている。EEPROM97には制御を行うためのプログラムとともに、各種規定値として、例えば、ヒータ32の発熱温度による複数の加熱温度として例えば、ヒータ温度Th1 に対し300℃、ヒータ温度Th2 に対し280℃、ヒータ温度Th3 に対し260℃、ヒータ温度Th4 に対し240℃が記憶されており、外部設定装置(PC:Personal Computer )100等を必要に応じて接続し、操作することにより自由にその内容や設定を変更することができる。この場合、最高加熱温度としてヒータ温度Th1 、最低加熱温度としてヒータ温度Th4 が設定され、その温度幅内に段階的に加熱温度として、ヒータ温度Th2 、Th3 が設定されている。そして、これらヒータ温度Th1 、Th2 、Th3 、Th4 のヒータ32の温度は処理槽4に加えられる加熱量を示すものである。 A control device 86 is provided as a control means for performing rotation control of the agitating motor 16, driving of the heater 32, and temperature control based on the operation command from the operation input device 94 and control information of the temperature sensors 34, 36, 66, 68 and the like. . The control device 86 is provided with, for example, a central processing unit (CPU) 96, an EEPROM 97, a RAM 98, and a timer 99. Further, the control device 86 inputs an operation command or the like for instructing operation from the operation input device 94, or the temperature sensors 34 and 36. , 66, 68 etc. are provided with an input unit 90, a heater 32, a stirring motor 16, a circulation fan motor 72, a radiating fan motor 56, a deodorizing heater 78 and the like. It has been. The EEPROM 97 includes a program for performing control and various specified values, for example, a plurality of heating temperatures based on the heat generation temperature of the heater 32, for example, 300 ° C. for the heater temperature Th 1 , 280 ° C. for the heater temperature Th 2 , heater 260 ° C. is stored for the temperature Th 3 and 240 ° C. for the heater temperature Th 4 , and the contents can be freely set by connecting and operating an external setting device (PC: Personal Computer) 100 or the like as necessary. Settings can be changed. In this case, the heater temperature Th 1 is set as the maximum heating temperature, the heater temperature Th 4 is set as the minimum heating temperature, and the heater temperatures Th 2 and Th 3 are set stepwise within the temperature range. The heater temperatures Th 1 , Th 2 , Th 3 and Th 4 indicate the amount of heating applied to the treatment tank 4.

ここで、生ごみ3の加熱乾燥において、その焦げ付きを防止しながら乾燥を行うためには焦げ付かない程度の加熱量で行うことが必要であり、その加熱量で最初から最後まで処理を行うと長時間を要することになるので、最初の加熱段階を最高加熱温度であるヒータ温度Th1 で加熱し、処理の進行に伴って徐々に加熱量を下げ、最終段階で焦げ付かない程度の加熱量として最低加熱温度であるヒータ温度Th4 に移行させる。即ち、それ以上同じ加熱量が加えられると焦げ付きが発生する前に加熱温度の切替えが必要となり、その加熱温度の切替えで生ごみ3の焦げ付きが防止されることになる。 Here, in the heat drying of the garbage 3, it is necessary to carry out with a heating amount that is not burnt in order to dry while preventing the burning, and when the treatment is performed from the beginning to the end with the heating amount. Since it takes a long time, the first heating stage is heated at the heater temperature Th 1 which is the maximum heating temperature, the heating amount is gradually lowered as the processing proceeds, and the heating quantity is such that it does not burn in the final stage. To the heater temperature Th 4 which is the minimum heating temperature. That is, if the same heating amount is applied further, it is necessary to switch the heating temperature before the burning occurs, and the burning 3 is prevented from burning by the switching of the heating temperature.

次に、生ごみ3の乾燥処理について、図3を参照して説明する。図3はヒータ温度、槽壁温度及びラジエターの入側温度・出側温度の変化を示すグラフである。   Next, the drying process of the garbage 3 is demonstrated with reference to FIG. FIG. 3 is a graph showing changes in heater temperature, tank wall temperature, and radiator inlet / outlet temperature.

最初の加熱段階であるヒータ温度Th1 での加熱段階において、槽壁温度は上昇した後、水分蒸発が活発化し、この場合、加熱量<蒸発熱量の関係から、槽壁温度は僅かに低下する。即ち、上昇後、下降し始めるときの最高温度をRAM98に記憶しておき、その後、所定時間T1 例えば、1回の生ごみ処理量が20kgの処理では30分、1回の生ごみ処理量が50kg又は80kgの処理では55分について、記憶した値を超えない場合、その値をピーク値Tndとして設定する。一旦下がった温度は生ごみ3の乾燥が進むにつれ、温度上昇を始めるが、一番下がった温度とピーク値Tndの差温を落ち込み温度差Tdownとして記憶する。温度上昇が進み、再びピーク値Tndに到達したとき、加熱熱量>蒸発熱量の状態になる。この状態での加熱量では槽壁温度は上昇を続け、生ごみ3が焦げ付く原因となるので、加熱量を下げる。このように生ごみ3の成分、即ち、その質や量が相違しても、生ごみ3に適した処理の切替ポイントを把握できる。 In the heating step at a heater temperature Th 1 is the first heating step, after the vessel wall temperature rose, moisture evaporation is activated, in this case, from the relationship of heating amount <evaporation heat, vessel wall temperature decreases slightly . That is, after rising, stores the maximum temperature at which starts to fall to the RAM 98, thereafter, the predetermined time T 1 for example, 30 minutes garbage disposal amount of 1 times in the process of 20 kg, one of the garbage throughput In the process of 50 kg or 80 kg, if the stored value is not exceeded for 55 minutes, that value is set as the peak value Tnd. The temperature once lowered starts to rise as drying of the garbage 3 proceeds, but the difference between the lowest temperature and the peak value Tnd falls and is stored as a temperature difference Tdown. When the temperature rises and reaches the peak value Tnd again, the heating heat quantity> the evaporation heat quantity is obtained. In the heating amount in this state, the tank wall temperature continues to rise and causes the garbage 3 to burn, so the heating amount is lowered. Thus, even if the components of the garbage 3, that is, the quality and quantity thereof are different, it is possible to grasp the processing switching points suitable for the garbage 3.

このような加熱温度を固定値とすれば、その温度になかなか達しないために大きな加熱量で乾燥を続けることとなり、焦げ付きの原因になる。また、固定値より高い温度が水分の蒸発に適する場合には、熱量不足のため、常に効率の悪い低い処理となり、全体的な処理時間が長く掛かり、非効率な処理となる。   If such a heating temperature is set to a fixed value, the temperature is not easily reached, so that drying is continued with a large heating amount, which causes burning. Further, when a temperature higher than the fixed value is suitable for the evaporation of moisture, the process is always inefficient and low because of the lack of heat, and the overall processing time is long, resulting in an inefficient process.

ピーク値Tndに達すると加熱量を段階的に下げる。即ち、段階的に加熱温度を下げると、加熱量が減少するため、槽壁温度は一旦下がるが、生ごみ3内の水分が蒸発により減少するため、再び上昇に転ずる。このような生ごみ3中の水分の減少とともに加熱量を減少させるため、高効率で乾燥を促進させ、焦げ付きの防止が図られる。   When the peak value Tnd is reached, the heating amount is lowered stepwise. That is, when the heating temperature is lowered step by step, the amount of heating is reduced, so that the tank wall temperature is temporarily lowered. However, since the water in the garbage 3 is reduced by evaporation, the temperature rises again. Since the amount of heating is reduced as the moisture in the garbage 3 is reduced, drying is promoted with high efficiency, and scorching is prevented.

槽壁温度がピーク値Tndより所定温度ΔT1 例えば、1回の生ごみの処理量が20kgの処理では5℃、1回の生ごみ処理量が50kg又は80kgの処理では4℃だけ低い温度Tns以下に低下すると、加熱量を上げる。これは、乾燥処理中に追加の生ごみ投入を行った際に発生する。追加投入された場合にも、効率的な生ごみ処理が可能なように制御する。また、追加投入を行わなくても、加熱量を下げたときに槽壁温度が下がりすぎる場合もある。これは、特に処理量が多いときに発生する場合があるが、加熱量がそのままでは非効率なので、このような場合に対しても加熱量を上げて対応する。 The tank wall temperature is lower than the peak value Tnd by a predetermined temperature ΔT 1, for example, a temperature Tns that is 5 ° C. when a single garbage processing amount is 20 kg, and a temperature Tns that is 4 ° C. when a single garbage processing amount is 50 kg or 80 kg. When it falls below, the heating amount is increased. This occurs when additional garbage is thrown in during the drying process. Control is also performed so that efficient garbage disposal is possible even when additional charging is performed. Even without additional charging, the tank wall temperature may be too low when the heating amount is lowered. This may occur particularly when the amount of processing is large, but since the heating amount is inefficient as it is, the heating amount is increased to cope with such a case.

加熱段階が最終段階であるヒータ温度Th4 での加熱段階に移行すると、ラジエター42の入側温度と出側温度とから両者の差温の変化を監視し、加熱終了の判断を行う。即ち、ラレジター42の入側温度と出側温度との差温は、ラジエター42を通過する蒸気40の熱交換により生じ、ラジエター42の入側温度は温度センサ66、その出側温度は温度センサ68で検出され、その差温が求められる。蒸気中の水分は凝縮水58となり排出される。入側温度と出側温度の差温は、外気温が低いほど、蒸気中の水分が少ないほど、大きくなる。 When the heating stage shifts to the heating stage at the heater temperature Th 4 which is the final stage, a change in the difference between the temperatures is monitored from the inlet side temperature and the outlet side temperature of the radiator 42 to determine the end of heating. That is, the temperature difference between the inlet side temperature and the outlet side temperature of the radiator 42 is generated by heat exchange of the steam 40 passing through the radiator 42. The inlet side temperature of the radiator 42 is the temperature sensor 66, and the outlet side temperature thereof is the temperature sensor 68. And the temperature difference is obtained. The moisture in the steam becomes condensed water 58 and is discharged. The difference temperature between the inlet side temperature and the outlet side temperature increases as the outside air temperature decreases and the moisture in the steam decreases.

そして、最終段階における最低加熱温度であるヒータ温度Th4 での加熱段階において、差温で完了を判断する際利用する乾燥途中の最大差温ΔTは、最終段階直前、即ち、ヒータ温度Th3 の加熱段階での差温で決定する。乾燥処理が長時間に亘ると、乾燥処理に環境温度が影響を与えることになるが、斯かる差温を用いれば、日中と夜間との温度差によるラジエター42の冷却能力の違い等が最終段階の判断に影響することが防止される。さらに、最終段階では乾燥処理が進んでおり、含水率のばらつきが少ないためである。また、このような差温を用いるため、季節の影響等も吸収することができる。そして、処理完了は最大差温ΔTより所定値αとして例えば2℃の差温が広がることにより判断される。 Then, in the heating stage at the heater temperature Th 4 which is the lowest heating temperature in the final stage, the maximum temperature difference ΔT during drying used when judging completion based on the differential temperature is the value immediately before the final stage, that is, the heater temperature Th 3 . It is determined by the temperature difference in the heating stage. If the drying process takes a long time, the environmental temperature will affect the drying process. If such a temperature difference is used, the difference in the cooling capacity of the radiator 42 due to the temperature difference between the daytime and the nighttime will be the final. It is prevented from affecting the judgment of the stage. Furthermore, it is because the drying process is progressing in the final stage and there is little dispersion | variation in a moisture content. Moreover, since such a differential temperature is used, the influence of a season, etc. can be absorbed. Then, the completion of the process is determined by a difference temperature of, for example, 2 ° C. spreading from the maximum temperature difference ΔT as a predetermined value α.

次に、生ごみ2の乾燥処理について、図4を参照して説明する。図4は生ごみの乾燥処理を示すフローチャートである。   Next, the drying process of the garbage 2 is demonstrated with reference to FIG. FIG. 4 is a flowchart showing the garbage drying process.

乾燥処理が開始されると、最高加熱温度であるヒータ温度Th1 で加熱を開始する(ステップS1)。このステップS1の後、ステップS2に至るまでの期間では、図3に示すように、ヒータ温度Th2 、Th3 等の昇降による加熱処理が行われ、最終段階に移行することになる。そこで、ラジエター42の差温の判断基準を設定する段階、即ち、最終段階である最低加熱温度としてのヒータ温度Th4 での加熱段階の直前段階のヒータ温度Th3 での加熱段階か否かの判断を行う(ステップS2)。差温の設定段階であるヒータ温度Th3 での加熱段階でなければステップS5に移行する。記憶済みの最大差温ΔTと読み込んだ差温を比較する(ステップS3)。記憶済みの最大差温ΔTの方が大きければステップS5に移行する。読み込んだ差温の方が大きい場合には、記憶済みの最大差温ΔTを読み込んだ差温に更新し、新たな最大差温ΔTとして記憶する(ステップS4)。 When the drying process is started, heating is started at the heater temperature Th 1 which is the maximum heating temperature (step S1). In the period from step S1 to step S2, as shown in FIG. 3, heat treatment is performed by raising and lowering the heater temperatures Th 2 , Th 3, etc., and the process proceeds to the final stage. Therefore, it is determined whether or not the heating stage at the heater temperature Th 3 immediately before the heating stage at the stage of setting the temperature difference judgment criteria of the radiator 42, that is, the heating stage at the heater temperature Th 4 as the lowest heating temperature as the final stage. A determination is made (step S2). If heating step at a heater temperature Th 3 is a setting stage differential temperature process proceeds to step S5. The stored maximum temperature difference ΔT is compared with the read temperature difference (step S3). If the stored maximum temperature difference ΔT is larger, the process proceeds to step S5. If the read temperature difference is larger, the stored maximum temperature difference ΔT is updated to the read temperature difference and stored as a new maximum temperature difference ΔT (step S4).

そして、加熱処理が最低加熱温度であるヒータ温度Th4 での加熱段階か否かを判断する(ステップS5)。ヒータ温度Th4 での加熱段階であればステップS10に移行する。最低加熱温度であるヒータ温度Th4 での加熱段階でない場合には、加熱段階が進むための加熱温度を下げる条件になったか否か、即ち、例えば、槽壁温度がピーク値Tndを超えたか否かを判断する(ステップS6)。加熱温度の下降切替え条件を満たしているときにはステップS12に移行する。加熱温度を下げる条件になっていない場合には、加熱温度を上昇する必要が発生したか否か、即ち、槽壁温度が下がりすぎていないかをチェックする(ステップS7)。必要が無ければ、即ち、ピーク値Tndより所定温度ΔT、例えば、1回の生ごみ処理量が20kgの処理では5℃、1回の生ごみ処理量が50kg又は80kgの処理では4℃だけ低い温度Tns以下に下がっていなければ、ステップS2に戻る。加熱温度の上昇切替えが必要と判定されると、現設定が最高加熱温度であるヒータ温度Th1 であるか否かが判定され(ステップS8)、ヒータ温度Th1 の設定である場合には、これ以上は加熱温度を高めることができないので、ステップS2に移行し、ヒータ温度Th1 の設定でなければステップS9に移行する。ステップS9では、ヒータ温度の設定を一段階上げて、加熱量を増加し、その加熱量変更後、ステップS2に戻る。 Then, it is determined whether or not the heating process is a heating stage at the heater temperature Th 4 which is the minimum heating temperature (step S5). If the heating stage is at the heater temperature Th 4 , the process proceeds to step S10. If it is not the heating stage at the heater temperature Th 4 that is the minimum heating temperature, whether or not the condition for lowering the heating temperature for the heating stage to be reached, that is, for example, whether or not the tank wall temperature exceeds the peak value Tnd Is determined (step S6). When the heating temperature lowering switching condition is satisfied, the process proceeds to step S12. If the condition for lowering the heating temperature is not satisfied, it is checked whether or not it is necessary to increase the heating temperature, that is, whether the tank wall temperature is too low (step S7). If not necessary, that is, a predetermined temperature ΔT lower than the peak value Tnd, for example, 5 ° C. in the case where the amount of garbage processing amount is 20 kg, and 4 ° C. in the case where the amount of garbage processing amount is 50 kg or 80 kg. If not lower than the temperature Tns, the process returns to step S2. If it is determined that heating temperature increase switching is necessary, it is determined whether or not the current setting is the heater temperature Th 1 that is the maximum heating temperature (step S8). If the heater temperature Th 1 is set, because more can not raise the heating temperature, the process proceeds to step S2, the process proceeds to step S9 if the setting of the heater temperature Th 1. In step S9, the heater temperature setting is increased by one stage, the heating amount is increased, and after the heating amount is changed, the process returns to step S2.

また、ステップS10では、ラジエター42の入側温度と出側温度との差温が最大差温ΔTより所定値α(例えば、2℃)大きくなるのを待つ。ラジエター42の差温が最大差温ΔTより所定値αだけ大きくなると、ステップS11に移行する。ステップS11では、ラジエター42の差温にて加熱処理終了の判断を行った場合の処理である。この結果、生ごみ加熱処理を終了する。   In step S10, the process waits for the temperature difference between the inlet side temperature and the outlet side temperature of the radiator 42 to be larger than the maximum temperature difference ΔT by a predetermined value α (for example, 2 ° C.). When the temperature difference of the radiator 42 becomes larger than the maximum temperature difference ΔT by a predetermined value α, the process proceeds to step S11. In step S11, it is a process at the time of determining completion | finish of a heat processing by the differential temperature of the radiator 42. FIG. As a result, the garbage heat treatment is finished.

ところで、ステップS6において、加熱温度を下げる条件が成立したとき、ヒータ温度設定を一段階下げ、加熱量を減少させる(ステップS12)。これは、このままの温度設定で加熱すると、生ごみ3に焦げ付きが発生するので、加熱量を減少させている。ヒータ温度設定を一段階下げることにより、槽壁温度は一旦下がるが、その後上昇傾向に転じる。また、この場合、最低加熱温度であるヒータ温度Th4 の直前段階、即ち、ヒータ温度Th3 での加熱段階であるか否かを判定し(ステップS13)、ヒータ温度Th4 の直前段階(ヒータ温度Th3 )にない場合にはステップS2に戻り、ヒータ温度Th4 の直前段階(ヒータ温度Th3 )の場合には、ラジエター42の最大差温ΔTの初期値として0℃を記憶し(ステップS14)、ステップS2に移行する。 By the way, when the condition for lowering the heating temperature is established in step S6, the heater temperature setting is lowered by one step to reduce the heating amount (step S12). This is because if the food is heated at the temperature setting as it is, the garbage 3 is burnt, so that the heating amount is reduced. By lowering the heater temperature setting by one step, the tank wall temperature is once lowered, but then it starts to rise. Further, in this case, it is determined whether or not it is a stage immediately before the heater temperature Th 4 which is the lowest heating temperature, that is, a heating stage at the heater temperature Th 3 (step S13), and a stage immediately before the heater temperature Th 4 (heater If it is not at the temperature Th 3 ), the process returns to step S2, and if it is immediately before the heater temperature Th 4 (heater temperature Th 3 ), 0 ° C. is stored as the initial value of the maximum temperature difference ΔT of the radiator 42 (step S14), the process proceeds to step S2.

このように、この実施形態では、乾燥処理の最終段階において、ラジエター42の出側、入側の温度差で乾燥処理終了の判断を行っており、その場合、最終段階の一段階前の時点における最大温度差を記憶し、その値+所定値にて乾燥終了の判断を行うので、乾燥処理の完了と加熱処理の終了とを合致させることができ、生ごみの質や量、さらには環境温度に影響を受けることなく、乾燥の均一性を高めることができる。   As described above, in this embodiment, in the final stage of the drying process, the end of the drying process is determined based on the temperature difference between the outlet side and the inlet side of the radiator 42. In this case, at the time point one stage before the final stage. Since the maximum temperature difference is stored and the end of drying is determined based on that value + a predetermined value, the completion of the drying process and the end of the heating process can be matched, and the quality and quantity of garbage, as well as the environmental temperature The uniformity of drying can be improved without being affected by the above.

実施形態では、最高加熱温度と最低加熱温度との間に段階的、不連続的な加熱温度を設定し、その加熱温度を最高加熱温度から最低加熱温度までの間で段階的に加熱温度を切り替える構成について説明したが、加熱温度の切替えは連続的な値で変更するようにしてもよい。   In the embodiment, a stepwise and discontinuous heating temperature is set between the maximum heating temperature and the minimum heating temperature, and the heating temperature is switched stepwise between the maximum heating temperature and the minimum heating temperature. Although the configuration has been described, the switching of the heating temperature may be changed with a continuous value.

また、実施形態では、乾燥終了を判定するため、最終段階に移行する前のラジエター42の入側温度と出側温度との最大差温又はその最大差温に所定値を加えた値を基準温度として用いているが、乾燥終了が判定可能な任意の値を基準温度として設定してもよい。   In the embodiment, in order to determine the end of drying, the reference temperature is a maximum temperature difference between the inlet side temperature and the outlet side temperature of the radiator 42 before the transition to the final stage, or a value obtained by adding a predetermined value to the maximum temperature difference. However, any value that can determine the end of drying may be set as the reference temperature.

以上説明したように、本発明の最も好ましい実施形態等について説明したが、本発明は、上記記載に限定されるものではなく、特許請求の範囲に記載され、又は明細書に開示された発明の要旨に基づき、当業者において様々な変形や変更が可能であることは勿論であり、斯かる変形や変更が、本発明の範囲に含まれることは言うまでもない。
As described above, the most preferable embodiment of the present invention has been described. However, the present invention is not limited to the above description, and is described in the claims or disclosed in the specification. It goes without saying that various modifications and changes can be made by those skilled in the art based on the gist, and such modifications and changes are included in the scope of the present invention.

本発明によれば、生ごみの種類や量又は外気温度等に影響されることなく、生ごみの乾燥の均一化を図ることができ、その肥料化や廃棄処理の容易化に寄与することができ、有用である。
According to the present invention, it is possible to achieve uniform drying of garbage without being affected by the type and amount of garbage or the outside air temperature, etc., and contribute to facilitating its fertilization and disposal. Can and is useful.

本発明の実施形態に係る生ごみ処理方法及びその装置を示す図である。It is a figure which shows the garbage processing method and its apparatus which concern on embodiment of this invention. 生ごみ処理装置の制御装置を示すブロック図である。It is a block diagram which shows the control apparatus of a garbage processing apparatus. ヒータ温度、槽壁温度及びラジエターの入側温度・出側温度の変化を示す図である。It is a figure which shows the change of heater temperature, tank wall temperature, and the entrance side temperature / outlet side temperature of a radiator. 生ごみの乾燥処理を示すフローチャートである。It is a flowchart which shows the drying process of garbage.

符号の説明Explanation of symbols

2 生ごみ処理装置
3 生ごみ
4 処理槽
32 ヒータ(加熱手段)
40 蒸気
42 ラジエター(凝縮手段)
44 循環路(循環手段)
58 凝縮水
66、68 温度センサ
86 制御装置(制御手段)
2 Garbage treatment equipment 3 Garbage 4 Treatment tank 32 Heater (heating means)
40 Steam 42 Radiator (condensing means)
44 Circuit (circulation means)
58 Condensed water 66, 68 Temperature sensor 86 Control device (control means)

Claims (3)

処理槽で加熱手段により加熱温度を初期段階で最高加熱温度、最終段階で最低加熱温度とし、その温度幅内で前記加熱温度を可変させて生ごみを加熱する処理と、
この加熱処理により前記処理槽で発生する蒸気を凝縮手段を通して凝縮水を分離するとともに、凝縮水が分離された蒸気を前記処理槽に循環させる処理と、
前記凝縮手段の前記蒸気の入側温度と出側温度とを検出する処理と、
前記最低加熱温度で加熱する場合に前記入側温度と前記出側温度との差温が基準温度を超えたとき、前記加熱処理を終了させる処理と、
を含むことを特徴とする生ごみ処理方法。
A process of heating the garbage by changing the heating temperature within the temperature range with the maximum heating temperature in the initial stage and the minimum heating temperature in the final stage by the heating means in the treatment tank,
A process of separating the condensed water from the steam generated in the processing tank by this heat treatment through the condensing means, and circulating the steam from which the condensed water has been separated to the processing tank;
A process of detecting an inlet side temperature and an outlet side temperature of the steam of the condensing means;
When the difference temperature between the inlet side temperature and the outlet side temperature exceeds a reference temperature when heating at the minimum heating temperature, a process of terminating the heating process;
Garbage disposal method characterized by including.
前記基準温度は、前記最低加熱温度に移行する前段階の加熱温度下で検出される前記入側温度と前記出側温度との最大差温又はこの最大差温に所定値を加えた値であることを特徴とする請求項1記載の生ごみ処理方法。   The reference temperature is a maximum temperature difference between the inlet side temperature and the outlet side temperature detected under the heating temperature of the previous stage before shifting to the minimum heating temperature, or a value obtained by adding a predetermined value to the maximum temperature difference. The garbage disposal method of Claim 1 characterized by the above-mentioned. 加熱手段を備え、装填された生ごみに加熱処理を施す処理槽と、
この処理槽で前記生ごみから発生する蒸気から凝縮水を分離する凝縮手段と、
この凝縮手段と前記処理槽との間に連結されて前記蒸気を前記凝縮手段に循環させる循環手段と、
前記凝縮手段の前記蒸気の入側温度と出側温度とを検出する温度検出手段と、
前記処理槽で前記加熱手段により加熱温度を初期段階で最高加熱温度、最終段階で最低加熱温度とし、その温度幅内で前記加熱温度を可変させて前記生ごみを加熱するとともに、前記最低加熱温度に移行する前の加熱温度下で前記入側温度と前記出側温度との差温に基準温度を設定し、前記最低加熱温度で加熱する場合に前記入側温度と前記出側温度との差温が前記基準温度を超えたとき、前記加熱処理を終了させる制御手段と、
を含むことを特徴とする生ごみ処理装置。
A treatment tank provided with a heating means, which heat-treats the loaded garbage;
Condensing means for separating condensed water from the steam generated from the garbage in this treatment tank;
A circulating means connected between the condensing means and the treatment tank to circulate the vapor to the condensing means;
Temperature detecting means for detecting an inlet side temperature and an outlet side temperature of the steam of the condensing means;
In the treatment tank, the heating temperature is set to the maximum heating temperature in the initial stage by the heating means and the minimum heating temperature in the final stage, and the heating temperature is varied within the temperature range to heat the garbage, and the minimum heating temperature The reference temperature is set to the difference temperature between the inlet side temperature and the outlet side temperature under the heating temperature before the transition to, and the difference between the inlet side temperature and the outlet side temperature when heating at the minimum heating temperature Control means for terminating the heat treatment when the temperature exceeds the reference temperature;
A garbage disposal apparatus comprising:
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101178572B1 (en) 2012-01-30 2012-08-30 (주) 대성이앤비 Apparatus for drying and reducing food waste and method to control the same
KR101930882B1 (en) * 2018-01-15 2018-12-19 주식회사 가이아 Apparatus for drying organic waste
CN112317511A (en) * 2020-10-19 2021-02-05 重庆市农业科学院 Small-size vertical aerobic fermentation system and push-pull shaking device thereof

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH085245A (en) * 1994-06-22 1996-01-12 Mitsubishi Electric Corp Drying machine, dehumidifying device of drying machine and cooler
JP2002355635A (en) * 2001-05-31 2002-12-10 Takagi Ind Co Ltd Garbage treatment method and apparatus

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH085245A (en) * 1994-06-22 1996-01-12 Mitsubishi Electric Corp Drying machine, dehumidifying device of drying machine and cooler
JP2002355635A (en) * 2001-05-31 2002-12-10 Takagi Ind Co Ltd Garbage treatment method and apparatus

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101178572B1 (en) 2012-01-30 2012-08-30 (주) 대성이앤비 Apparatus for drying and reducing food waste and method to control the same
KR101930882B1 (en) * 2018-01-15 2018-12-19 주식회사 가이아 Apparatus for drying organic waste
CN112317511A (en) * 2020-10-19 2021-02-05 重庆市农业科学院 Small-size vertical aerobic fermentation system and push-pull shaking device thereof

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