JPH06292875A - Garbage processing equipment - Google Patents
Garbage processing equipmentInfo
- Publication number
- JPH06292875A JPH06292875A JP5107700A JP10770093A JPH06292875A JP H06292875 A JPH06292875 A JP H06292875A JP 5107700 A JP5107700 A JP 5107700A JP 10770093 A JP10770093 A JP 10770093A JP H06292875 A JPH06292875 A JP H06292875A
- Authority
- JP
- Japan
- Prior art keywords
- burner
- fermenter
- air
- furnace
- garbage
- 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
Links
Landscapes
- Processing Of Solid Wastes (AREA)
- Refuse Collection And Transfer (AREA)
Abstract
(57)【要約】
【目的】 燃料費を節減しつつ二次公害を防止する。
【構成】 バーナ16で加熱された脱臭炉15内の空気
が処理炉本体1内に流入して発酵槽3を70〜90度に
昇温させ、発酵槽3内では発酵菌の増殖により生ゴミの
発酵・分解・乾燥が進み、その処理は3時間程度で終了
する。発酵槽3内で生じる水蒸気、粉塵、悪臭成分は脱
臭炉15においてバーナ16により700〜900度に
加熱され、水蒸気が視認できないほどの微粒状になると
ともに粉塵と悪臭成分が焼き切られる。
【効果】 排気中には水蒸気の白煙、粉塵、悪臭がな
く、生ゴミ処理にともなう二次公害が防止される。しか
も、その二次公害防止用のバーナの排熱を流用して生ゴ
ミを昇温させ、かつ、発酵槽を下側から効率的に加熱す
るから、バーナの燃料消費量が少なくて済む。
(57) [Summary] [Purpose] To prevent secondary pollution while reducing fuel costs. [Structure] The air in the deodorizing furnace 15 heated by the burner 16 flows into the processing furnace main body 1 to raise the temperature of the fermenter 3 to 70 to 90 degrees, and in the fermenter 3, growth of fermenting bacteria causes raw garbage. Fermentation, decomposition, and drying proceed in about 3 hours. The steam, dust, and malodorous components generated in the fermenter 3 are heated in the deodorization furnace 15 by the burner 16 to 700 to 900 ° C., and the vapor becomes fine particles invisible and the dust and malodorous components are burned out. [Effect] There is no white smoke, dust, or odor of water vapor in the exhaust gas, and the secondary pollution associated with garbage processing is prevented. Moreover, since the waste heat of the burner for secondary pollution prevention is diverted to raise the temperature of the garbage and the fermentation tank is efficiently heated from the lower side, the fuel consumption of the burner can be reduced.
Description
【0001】[0001]
【産業上の利用分野】本発明は、主として食堂やレスト
ランなどから排出される業務用生ゴミを、70〜80度
という比較的に高い温度で、高温発酵菌を使つて発酵・
分解・乾燥を行つて、肥料や飼料として有効に利用する
ことができるように処理するための生ゴミ処理装置に関
するものである。BACKGROUND OF THE INVENTION The present invention is a method for fermenting industrial garbage, which is mainly discharged from restaurants and restaurants, at a relatively high temperature of 70 to 80 degrees Celsius using high temperature fermenting bacteria.
The present invention relates to an apparatus for disposing of garbage that is decomposed and dried so that it can be effectively used as fertilizer or feed.
【0002】[0002]
【従来の技術】一般に、食堂やレストランなどから排出
される業務用生ゴミは、そのほとんどが、焼却または埋
め立てのかたちで処分されているが、生ゴミには蛋白質
などの有機質物が含まれていて、その有効利用を図るこ
とが可能である。2. Description of the Related Art Generally, most of the industrial garbage discharged from restaurants and restaurants is disposed of by incineration or landfill, but the organic garbage such as protein is contained in the garbage. It is possible to make effective use of it.
【0003】このため、生ゴミを発酵槽の中に入れ、常
温、中温(40〜60度)あるいは高温(70〜90
度)に加熱し、夫々の温度に適した発酵菌を投入して、
生ゴミを発酵・分解・乾燥させることにより、生ゴミを
取り扱いが容易な粉末顆粒状にして回収するようにした
生ゴミ処理装置が創案された。For this reason, raw garbage is put in a fermenter and kept at room temperature, medium temperature (40-60 degrees) or high temperature (70-90).
Temperature) and put fermenting bacteria suitable for each temperature,
A raw garbage processing device was devised, in which the raw garbage was collected in the form of powder granules that were easy to handle by fermenting, decomposing, and drying the raw garbage.
【0004】このような生ゴミ処理装置においては、生
ゴミの乾燥にともなつて発生浮遊する水蒸気、粉塵、悪
臭成分が発酵槽から排出される空気の中に含まれるが、
その排出される空気をそのまま大気中に放出してしまう
と、不快感を与える水蒸気の白煙が立ち昇つたり粉塵や
悪臭が漂つたりするという二次公害が発生することとな
るため、排出される空気に加熱処理を施して無公害状態
にするための脱臭炉を設ける必要がある。In such an apparatus for treating food waste, water vapor, dust, and malodorous components that are generated and suspended as the food waste is dried are contained in the air discharged from the fermentation tank.
If the discharged air is released into the atmosphere as it is, secondary pollution such as white smoke of water vapor, which causes discomfort, rises, and dust and foul odors are generated. It is necessary to provide a deodorizing furnace to heat the generated air to a pollution-free state.
【0005】[0005]
【発明が解決しようとする課題】脱臭炉を設けた生ゴミ
処理装置として、従来は、発酵槽、発酵槽加熱用バー
ナ、発酵槽内の空気の排出経路に設けた脱臭炉、及び、
脱臭炉加熱用バーナから構成したものが公知である。か
かる装置は、発酵槽内の生ゴミを発酵槽加熱用バーナに
よつて昇温させることにより発酵・分解・乾燥処理し、
この発酵槽から排出される空気中の水蒸気、粉塵、悪臭
成分を脱臭炉内において脱臭炉加熱用バーナで700〜
900度に加熱し、水蒸気を視認できないほどの微粒状
にするとともに粉塵と悪臭成分を焼き切り、これによつ
て、不快感を与える水蒸気の白煙が立ち昇つたり粉塵や
悪臭が漂つたりするという生ゴミ処理にともなう二次公
害の発生を防止するようになつている。As a raw garbage processing apparatus provided with a deodorizing furnace, conventionally, a fermenter, a burner for heating the fermenting tank, a deodorizing furnace provided in an air discharge path in the fermenting tank, and
A burner for heating a deodorizing furnace is known. Such an apparatus performs fermentation / decomposition / drying treatment by raising the temperature of raw garbage in the fermenter with a burner for heating the fermenter,
The steam, dust, and malodorous components in the air discharged from this fermenter are heated in the deodorizing furnace by a burner for heating the deodorizing furnace from 700 to
When heated to 900 degrees, the water vapor is made into fine particles that are invisible, and dust and malodorous components are burned out. This causes white smoke of water vapor, which causes discomfort, to rise and dust and malodors to drift. The secondary pollution caused by the garbage disposal is prevented.
【0006】しかしながら、上記の生ゴミ処理装置は、
生ゴミの分解・発酵・乾燥処理を行うためのバーナ及び
二次公害を防止するためのバーナとして夫々専用のもの
を用いており、このために、バーナの燃料費が高くつく
という欠点があつた。しかも、発酵槽加熱用のバーナは
発酵槽を上側から加熱するようになつていたため、加熱
効率が悪く、この点もバーナの燃料費が高くつく原因と
なつていた。However, the above-mentioned garbage processing device is
A burner for decomposing / fermenting / drying garbage and a burner for preventing secondary pollution are used respectively, which has the drawback of high fuel cost for the burner. . Moreover, since the burner for heating the fermenter was designed to heat the fermenter from the upper side, the heating efficiency was poor, and this also contributed to the high fuel cost of the burner.
【0007】本発明は、このような事情に鑑みて創案さ
れたものであり、燃料費の節減を図りつつ二次公害の防
止を行うことができるようにした生ゴミ処理装置を提供
することを目的とするものである。The present invention was devised in view of the above circumstances, and it is an object of the present invention to provide a garbage disposal device capable of preventing secondary pollution while reducing fuel costs. It is intended.
【0008】[0008]
【課題を解決するための手段】上記課題を解決するため
の手段として、請求項1に記載の発明は、処理炉本体内
に設けられて内部に駆動機構により回転する攪拌翼を備
えた発酵槽と、内部の空気を加熱するバーナを備えた脱
臭炉と、その脱臭炉内の空気を処理炉本体内の発酵槽よ
りも下方空間に導入する導入路と、発酵槽内の空気を脱
臭炉内に還流させる還流路と、脱臭炉内の空気を外部に
排出させる排気路とから構成した。As a means for solving the above-mentioned problems, the invention according to claim 1 is a fermentation tank provided in a main body of a processing furnace and internally provided with a stirring blade rotated by a drive mechanism. And a deodorizing furnace equipped with a burner for heating the internal air, an introduction path for introducing the air in the deodorizing furnace into the space below the fermentation tank in the processing furnace body, and the air in the fermentation tank in the deodorizing furnace. And a discharge path for discharging the air in the deodorizing furnace to the outside.
【0009】請求項2に記載の発明は、請求項1に記載
の発明において、処理炉本体内において発酵槽を下から
加熱するサブバーナを設けた構成とした。According to a second aspect of the present invention, in the first aspect of the invention, a subburner for heating the fermentation tank from below is provided in the processing furnace body.
【0010】請求項3に記載の発明は、請求項1または
請求項2に記載の発明において、低温の空気流を排気路
中に吹き出す冷却フアンを設けた構成とした。According to a third aspect of the present invention, in the first or second aspect of the invention, a cooling fan for blowing a low temperature air flow into the exhaust passage is provided.
【0011】[0011]
【発明の作用及び効果】請求項1に記載の発明において
は、生ゴミの処理を行う際には、まず、発酵槽内に生ゴ
ミ、適量の発酵菌、及び、必要に応じて乾燥おから等の
水分調整剤を投入して、これらを攪拌翼によつて攪拌
し、バーナを点火する。このバーナの点火により脱臭炉
内の空気が700〜900度の高温に加熱され、加熱さ
れた空気の一部は熱風となつて導入路を通ることにより
処理炉本体内の発酵槽よりも下方空間に流入する。In the invention described in claim 1, when the raw garbage is treated, first, the raw garbage, an appropriate amount of fermenting bacteria, and, if necessary, dried okara are put in the fermenter. A water conditioner such as the above is added, and these are stirred by a stirring blade to ignite the burner. The ignition of this burner heats the air in the deodorization furnace to a high temperature of 700 to 900 degrees Celsius, and a part of the heated air passes through the introduction path by being combined with hot air, so that the space below the fermentation tank in the processing furnace body is lower. Flow into.
【0012】この流入した熱風により発酵槽がその下側
から加熱される。このとき、熱風は上記のように700
〜900度の高温に熱せられていたものであつて十分な
熱量を有していることから、発酵槽及び発酵槽内の生ゴ
ミは70〜90度の高温に昇温され、発酵菌の増殖によ
つて生ゴミの発酵・分解・乾燥が進む。発酵槽内におけ
る生ゴミの処理は、70〜90度の高温で行われるた
め、加熱を開始してから約3時間程度の短い時間で終了
する。処理が完了したら、発酵槽内の粉末顆粒状の処理
済み物を冷却した後に回収する。The fermenter is heated from the lower side by the inflowing hot air. At this time, the hot air is 700
Since it was heated to a high temperature of ~ 900 degrees and has a sufficient amount of heat, the fermenter and the garbage in the fermenter are heated to a high temperature of 70 to 90 degrees, and the fermentation bacteria grow. This promotes the fermentation, decomposition and drying of raw garbage. Since the processing of raw garbage in the fermenter is performed at a high temperature of 70 to 90 degrees, it is completed within a short time of about 3 hours after the heating is started. When the treatment is completed, the treated powdery granular material in the fermenter is cooled and then collected.
【0013】発酵槽内で生ゴミの発酵・分解・乾燥の処
理が行われている間、生ゴミ中の水分が気化して生じる
水蒸気及び生ゴミの乾燥にともなつて浮遊する粉塵や悪
臭成分は発酵槽内の空気とともに還流路を通つて脱臭炉
に流れ込む。脱臭炉内においては、流入する空気がバー
ナで700〜900度に加熱されることにより、その流
入する空気中の水蒸気が視認できないほどの微粒状にな
るとともに粉塵と悪臭成分が焼き切られる。このように
して脱臭炉内で無公害処理された空気は排気路を通して
大気中に放出されるが、このときに、不快感を与える水
蒸気の白煙が立ち昇つたり周囲に粉塵や悪臭が漂うこと
がない。During the processing of fermentation, decomposition and drying of raw garbage in the fermenter, water vapor generated by vaporization of water in the raw garbage and dust and malodorous components floating with the drying of the raw garbage Flows into the deodorizing furnace through the reflux passage together with the air in the fermenter. In the deodorizing furnace, when the inflowing air is heated to 700 to 900 degrees by the burner, the water vapor in the inflowing air becomes fine particles that cannot be visually recognized, and the dust and the malodorous component are burned out. The air thus treated as pollution-free in the deodorizing furnace is discharged into the atmosphere through the exhaust passage, but at this time, white smoke of water vapor, which gives an unpleasant feeling, rises and dust and bad odors drift around. Never.
【0014】上述のように、請求項1に記載の発明にお
いては、排気に際して不快感を与える水蒸気の白煙が立
ち昇つたり周囲に粉塵や悪臭が漂うことがなく、生ゴミ
処理にともなう二次公害の発生が防止されている。As described above, according to the first aspect of the present invention, white smoke of water vapor, which gives an unpleasant sensation when exhausting, does not rise and dust or a bad odor does not drift around, so that it is not necessary to dispose of garbage. The occurrence of secondary pollution is prevented.
【0015】しかも、発酵槽内の生ゴミを昇温させるた
めの加熱源として、生ゴミ昇温専用の加熱源を設けるの
ではなく、二次公害防止用の加熱源であるバーナの排熱
を流用し、かつ、発酵槽への加熱を発酵槽の上側からで
はなく発酵槽の下側から行うことによつて加熱効率の向
上を図るようになつているのであつて、これにより、バ
ーナの燃料消費量が比較的少なくて済んでいる。Moreover, as a heating source for raising the temperature of the raw garbage in the fermenter, a heat source dedicated to raising the temperature of the raw garbage is not provided, but exhaust heat of the burner which is a heating source for preventing secondary pollution is used. It is designed to improve the heating efficiency by diverting and heating the fermenter from the lower side of the fermenter rather than from the upper side of the fermenter. It consumes relatively little.
【0016】すなわち、請求項1に記載の発明によれ
ば、燃料費の節減を図りつつ二次公害の発生を防止する
ことができるという効果がある。That is, according to the invention as set forth in claim 1, there is an effect that the generation of secondary pollution can be prevented while reducing the fuel cost.
【0017】また、請求項2に記載の発明においては、
発酵槽をその下側から加熱するためのサブバーナを設け
たから、発酵槽が大型であつて脱臭炉からの排熱だけで
は発酵槽内の生ゴミを昇温させるのに不十分である場合
でも、生ゴミを70〜90度の高温にまで昇温させるこ
とが可能となり、生ゴミの発酵・分解・乾燥処理に要す
る時間を短くすることができるという効果がある。Further, in the invention described in claim 2,
Since the subburner for heating the fermenter from its lower side is provided, even if the fermenter is large and the exhaust heat from the deodorizing furnace is not sufficient to raise the temperature of the raw garbage in the fermenter, It is possible to raise the temperature of raw garbage to a high temperature of 70 to 90 degrees, and it is possible to shorten the time required for the fermentation, decomposition and drying treatment of raw garbage.
【0018】さらに、請求項3に記載の発明において
は、冷却フアンが設けられていて排気路中に低温の空気
が吹き出されるようになつているため、脱臭炉内で無公
害処理された高温の空気は、冷却フアンからの低温空気
に触れることによつて100〜150度程度の温度に冷
却された状態で排出されるのであり、空気の排出口の周
囲が高温に曝されるのを防止することができるという効
果がある。Further, in the invention according to the third aspect, since the cooling fan is provided so that the low temperature air is blown into the exhaust passage, the high temperature which is treated without pollution in the deodorizing furnace. Air is discharged in a state of being cooled to a temperature of about 100 to 150 degrees by touching the low temperature air from the cooling fan, so that the area around the air outlet is not exposed to high temperature. There is an effect that can be done.
【0019】[0019]
【実施例】以下、本発明の一実施例を添付図面に基づい
て説明する。処理炉本体1は断熱性を有する板材によつ
て構成されており、その内部には、処理炉本体1外へ開
口する図示しない蓋付きの投入口及び回収口を備えた発
酵槽3が、その側面及び下面と処理炉本体1との間に流
通空間を空けた状態で固設されている。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the accompanying drawings. The processing furnace main body 1 is constituted by a plate material having a heat insulating property. Inside the processing furnace main body 1, there is provided a fermenter 3 provided with an input port and a recovery port with a lid (not shown) with a lid. It is fixedly installed with a distribution space between the side and bottom surfaces and the processing furnace body 1.
【0020】発酵槽3の内部には駆動軸4に支持された
攪拌翼5が収容されており、この攪拌翼5は、処理炉本
体1の外部に設けたモータ(本発明の構成要素である駆
動機構に相当する)6の駆動によりスプロケツト7、8
及びチエーン9を介して連動する駆動軸4と一体に回転
するようになつている。また、発酵槽3には、発酵槽3
内と処理炉本体1内とを連通させる連通口10が形成さ
れているとともに、発酵槽3内の処理物の温度を測定す
るための処理物温度センサ11が設けられている。Inside the fermenter 3, a stirring blade 5 supported by a drive shaft 4 is housed, and the stirring blade 5 is a motor provided outside the processing furnace main body 1 (which is a component of the present invention). (Corresponding to a driving mechanism) 6 drives the sprockets 7 and 8
Also, it is adapted to rotate integrally with the drive shaft 4 which is interlocked via the chain 9. In addition, the fermenter 3 includes the fermenter 3
A communication port 10 for communicating the inside with the inside of the processing furnace main body 1 is formed, and a processed product temperature sensor 11 for measuring the temperature of the processed product in the fermenter 3 is provided.
【0021】処理炉本体1の上方には、断熱性材によつ
て箱形に成形された二次公害防止用の脱臭炉15が設け
られており、この脱臭炉15には、脱臭炉15内に向け
て火炎を噴出するバーナ16が設けられている。A deodorizing furnace 15 for preventing secondary pollution, which is formed in a box shape by a heat insulating material, is provided above the processing furnace body 1. The deodorizing furnace 15 has a deodorizing furnace inside. A burner 16 for ejecting a flame toward is provided.
【0022】脱臭炉15と処理炉本体1との間には、両
端が脱臭炉15のバーナ16から遠い位置に流入口17
aとして開口するとともに処理炉本体1の発酵槽3の底
部と対応する下部位置に流出口17bとして開口する導
入路17が設けられている。この導入路17の途中に
は、導入路17内に外気を流入させるための外気流入口
20が形成されている。Between the deodorizing furnace 15 and the processing furnace main body 1, both ends of the deodorizing furnace 15 are located at positions far from the burner 16 of the deodorizing furnace 15.
An introduction path 17 is provided at a lower position corresponding to the bottom of the fermenter 3 of the processing furnace main body 1 while opening as a. An outside airflow inlet 20 for allowing outside air to flow into the introduction passage 17 is formed in the middle of the introduction passage 17.
【0023】この導入路17と外気流入口20の分岐位
置にはダンパ31が設けられており、このダンパ31
は、外気流入口20から導入路17への外気の導入を阻
止するとともに脱臭炉15から処理炉本体1への空気の
流通を可能にする状態と、脱臭炉15から処理炉本体1
への流通を阻止するとともに外気流入口20から導入路
17を通して外気を処理炉本体1に導入させる状態とで
切り換えられるようになつている。A damper 31 is provided at a branch position between the introduction passage 17 and the outside air inlet 20, and the damper 31 is provided.
Is a state in which the introduction of the outside air from the outside airflow inlet 20 to the introduction passage 17 is prevented and the air can flow from the deodorization furnace 15 to the processing furnace main body 1, and a state where the deodorization furnace 15 and the processing furnace body 1
It is designed to be switched between a state in which the outside air is introduced into the processing furnace main body 1 from the outside airflow inlet 20 through the introduction path 17 while being prevented from flowing into the processing furnace main body 1.
【0024】また、導入路17の脱臭炉15内に開口す
る流入口17aには、脱臭炉15から導入路17に流入
する空気の温度を測定するための空気温度センサ22が
設けられている。An air temperature sensor 22 for measuring the temperature of the air flowing from the deodorizing furnace 15 into the introducing passage 17 is provided at the inflow port 17a of the introducing passage 17 which opens into the deodorizing furnace 15.
【0025】導入路17には、その脱臭炉15に開口す
る流入口17aに近い位置から分岐する排気路23が設
けられている。この排気路23の途中の縮径した部分に
は、冷却フアン26から送出された低温の空気を排気口
25側へ向けて吹き出す冷風吹出口27が設けられてい
る。The introduction passage 17 is provided with an exhaust passage 23 branching from a position near the inflow port 17a opening in the deodorizing furnace 15. A cold air outlet 27 that blows out the low-temperature air sent from the cooling fan 26 toward the exhaust port 25 side is provided in a part of the exhaust passage 23 where the diameter is reduced.
【0026】脱臭炉15と発酵槽3との間には、両端が
発酵槽3に流入口29aとして開口するとともに脱臭炉
15のバーナ16に近い位置に流出口29bとして開口
し、途中に還流フアン30を備えた還流路29が設けら
れている。Between the deodorizing furnace 15 and the fermentation tank 3, both ends are opened to the fermentation tank 3 as inlets 29a, and to the position near the burner 16 of the deodorizing furnace 15 as outlets 29b. A return path 29 with 30 is provided.
【0027】次に、本実施例の作用を説明する。まず、
投入口を開けて発酵槽3内に生ゴミと適量の発酵菌を投
入する。使用する発酵菌としては、島本微生物工業株式
会社製の「バイムフード」等が好適であるが、その外
に、好気性の高温発酵菌を主体にした多種類の微生物の
混合体を使用することもできる。さらに、生ゴミの水分
が多い場合には、乾燥おからや米糠等を水分調整剤とし
て投入する。Next, the operation of this embodiment will be described. First,
The charging port is opened and raw garbage and an appropriate amount of fermenting bacteria are charged into the fermenter 3. As the fermenting bacterium to be used, "Bime Food" manufactured by Shimamoto Microorganism Industry Co., Ltd. and the like are preferable, but in addition to that, it is also possible to use a mixture of various types of microorganisms mainly composed of aerobic high temperature fermenting bacterium. it can. Furthermore, when the water content of raw garbage is high, dried okara, rice bran, etc. are added as a water content adjusting agent.
【0028】次に、ダンパ31を、外気流入口20から
導入路17への外気の導入を阻止するとともに脱臭炉1
5から処理炉本体1への空気の流通を可能にする状態と
し、モータ6を駆動することにより発酵槽3内の攪拌翼
5を回転させ、脱臭炉15のバーナ16に点火し、還流
路29の還流フアン30と排気路23の冷却フアン26
を作動させる。Next, the damper 31 is used to prevent the introduction of the outside air from the outside airflow inlet 20 into the introduction passage 17 and to deodorize the furnace 1.
5, the stirring blade 5 in the fermentation tank 3 is rotated by driving the motor 6 to ignite the burner 16 of the deodorizing furnace 15, and the reflux path 29 Recirculation fan 30 and cooling fan 26 of exhaust passage 23
Operate.
【0029】脱臭炉15内の空気は、バーナ16によつ
て700〜900度の高温に加熱される。この加熱され
た空気の一部は、熱風となり、導入路17を通つて処理
炉本体1内に流入し、連通口10を通つて発酵槽2内に
流入し、還流路29を通つて脱臭炉15内に戻るという
経路で循環する。The air in the deodorizing furnace 15 is heated to a high temperature of 700 to 900 degrees by the burner 16. A part of the heated air becomes hot air, flows into the processing furnace main body 1 through the introduction path 17, flows into the fermentation tank 2 through the communication port 10, and passes through the reflux path 29 to deodorize the furnace. It circulates by the route of returning to the inside of 15.
【0030】発酵槽3内の生ゴミは、攪拌翼5で攪拌さ
れることによつて粉砕されつつ、処理炉本体1内におい
て発酵槽3の外底面と外側面を外部から包み込む熱風、
及び、発酵槽3内に流入して生ゴミと混合する熱風によ
つて70〜90度の温度に昇温される。The raw garbage in the fermenter 3 is crushed by being stirred by the agitating blades 5 and is heated by the hot air to wrap the outer bottom surface and the outer surface of the fermenter 3 in the processing furnace main body 1 from the outside,
And, the temperature is raised to 70 to 90 degrees by the hot air flowing into the fermenter 3 and mixed with the garbage.
【0031】発酵槽15内においては、生ゴミの温度が
70〜90度に保たれ、発酵菌の増殖によつて生ゴミの
発酵・分解・乾燥が進む。かかる発酵・分解・乾燥の処
理は70〜90度という比較的高い温度で行われるた
め、加熱を開始してから約3時間程度の短い時間で完了
する。In the fermenter 15, the temperature of raw garbage is maintained at 70 to 90 ° C., and the fermentation, decomposition and drying of raw garbage proceed due to the growth of fermenting bacteria. Since the fermentation, decomposition, and drying processes are carried out at a relatively high temperature of 70 to 90 degrees, they are completed within a short time of about 3 hours after the heating is started.
【0032】処理完了後は、バーナ16の点火と攪拌翼
5による攪拌を続けたままで、ダンパ31を切り換え
て、脱臭炉15から処理炉本体1への熱風の流入を阻止
するとともに外気流入口20から導入路17を通して外
気を処理炉本体1に導入させる状態とする。これによ
り、脱臭炉15からの排熱による発酵槽3への加熱が停
止するとともに、処理炉本体1内に流入する低温の外気
により発酵槽3及びその発酵槽3内に残つた粉末顆粒状
の処理済み物が冷却される。そして、この冷却を約15
分行つた後に、処理済み物を回収する。After the treatment is completed, the damper 31 is switched while keeping the ignition of the burner 16 and the stirring blade 5 stirring to prevent the hot air from flowing from the deodorizing furnace 15 into the processing furnace main body 1 and the outside airflow inlet 20. Then, the outside air is introduced into the processing furnace main body 1 through the introduction passage 17. As a result, the heating of the fermentation tank 3 due to the exhaust heat from the deodorizing furnace 15 is stopped, and the fermentation tank 3 and the powder granules remaining in the fermentation tank 3 due to the low temperature outside air flowing into the processing furnace main body 1 are stopped. The processed material is cooled. And this cooling is about 15
After the separation, the processed product is collected.
【0033】また、発酵槽3内で発酵・分解・乾燥の処
理が進行している間、及び、これらの処理が完了してか
ら処理済み物を回収するまでの冷却が行われている間、
生ゴミ中の水分が気化して生じる水蒸気及び生ゴミの乾
燥にともなつて浮遊する粉塵と悪臭成分は、発酵槽3内
の空気とともに還流路29を通つて脱臭炉15内に流入
する。While the fermentation, decomposition, and drying processes are in progress in the fermenter 3, and during the cooling from the completion of these processes to the collection of the processed products,
Water vapor generated by vaporization of water in the garbage and dust and malodorous components floating with the drying of the garbage flow into the deodorizing furnace 15 through the reflux passage 29 together with the air in the fermentation tank 3.
【0034】脱臭炉15内においては、流入する空気中
の水蒸気がバーナ16で加熱されることにより700〜
900度の高温となつて視認できないほどの微粒状にな
るとともに、流入する空気中の粉塵と悪臭成分がバーナ
16により焼き切られる。In the deodorizing furnace 15, the steam in the inflowing air is heated by the burner 16 to 700 to
At a high temperature of 900 degrees, it becomes invisible fine particles, and dust and odorous components in the inflowing air are burned out by the burner 16.
【0035】このように脱臭炉15内で加熱処理された
処理済み空気は、排気路23を通して大気中に放出され
るのであるが、排気に際しては、排気口25から不快感
を与える水蒸気の白煙が立ち昇つたり周囲に粉塵や悪臭
が漂うという二次公害が発生することはない。The treated air thus heat-treated in the deodorizing furnace 15 is discharged into the atmosphere through the exhaust passage 23. At the time of exhaust, white smoke of water vapor which gives offensiveness from the exhaust port 25. There will be no secondary pollution such as rising up and dust and bad odors around.
【0036】また、排出される処理済み空気は、冷却フ
アン26から送出されて排気路23中の冷風吹出口27
から吹き出す低温の空気のエジエクタ作用により吸い出
されてその空気と混合することにより、100〜150
度の低い温度になつた状態で排出されるため、排気口2
5の周囲が高温に曝されるということがない。The treated air to be discharged is sent out from the cooling fan 26 and the cold air outlet 27 in the exhaust passage 23.
100 to 150 by being sucked out by the eclectic action of the low-temperature air blown from the air and mixed with the air.
Since it is discharged in the condition that the temperature is low, the exhaust port 2
The area around 5 is not exposed to high temperatures.
【0037】上述のように、発酵槽3内の生ゴミを昇温
させるための加熱源として、生ゴミ昇温専用のバーナを
設けるのではなく、二次公害防止用の脱臭炉15のバー
ナ16の排熱が流用されており、しかも、発酵槽3への
加熱を発酵槽3の上側からではなく発酵槽3の下側と側
方とから行うことによつて加熱効率の向上が図られてい
る。したがつて、燃料消費量が少なくて済み、生ゴミの
処理に要するコスト、及び、生ゴミ処理にともなう二次
公害発生の防止に要するコストが低く抑えられている。As described above, the burner 16 of the deodorizing furnace 15 for preventing secondary pollution is not provided as a heating source for raising the temperature of the raw garbage in the fermenter 3 but a burner dedicated to raising the temperature of the raw garbage is provided. Waste heat is diverted, and the heating efficiency is improved by heating the fermentation tank 3 not from the upper side of the fermentation tank 3 but from the lower side and the side of the fermentation tank 3. There is. Therefore, the fuel consumption amount is small, the cost required for the treatment of raw garbage and the cost required for preventing the occurrence of secondary pollution due to the treatment of raw garbage are kept low.
【0038】本実施例においては、脱臭炉15内で加熱
焼却処理された高温の空気を排出時に冷却するための手
段として冷却フアン25を用いたが、これに代えて、排
気路23を長い煙突状にするようにしてもよい。この場
合にも、長い煙突状にしたことによつて空気の引き取り
力が強くなることにより、排気冷却の効果を得ることが
できる。In the present embodiment, the cooling fan 25 is used as a means for cooling the high temperature air that has been heated and incinerated in the deodorizing furnace 15 at the time of discharge, but instead of this, the exhaust passage 23 has a long chimney. You may make it into a shape. Also in this case, since the air collecting force is increased due to the long chimney shape, the effect of cooling the exhaust gas can be obtained.
【0039】なお、発酵槽3が大型であつて脱臭炉15
からの排熱だけでは生ゴミを40〜60度の中温にまで
しか昇温させることができない場合には、生ゴミの発酵
・分解・乾燥の処理に要する時間が長くかかる。したが
つて、このような場合には、処理炉本体1に、その処理
炉本体1の内部の発酵槽3よりも下方位置において火炎
を噴出するサブバーナ2を設けるようにすればよい。こ
のサブバーナ2の熱と脱臭炉15からの排熱の両方によ
つて発酵槽3を加熱することにより、発酵槽3内の生ゴ
ミを70〜90度の高温に昇温させ、生ゴミの発酵・分
解・乾燥処理に要する時間を短くすることが可能とな
る。The fermentation tank 3 is large and the deodorizing furnace 15 is used.
When it is possible to raise the temperature of the food waste only to a medium temperature of 40 to 60 degrees by only the exhaust heat from the above, it takes a long time to process the fermentation, decomposition and drying of the food waste. Therefore, in such a case, the processing furnace main body 1 may be provided with the sub-burner 2 for ejecting the flame at a position below the fermentation tank 3 inside the processing furnace main body 1. By heating the fermentation tank 3 with both the heat of the subburner 2 and the exhaust heat from the deodorizing furnace 15, the temperature of the raw garbage in the fermentation tank 3 is raised to a high temperature of 70 to 90 degrees, and the fermentation of the raw garbage is performed. -It is possible to shorten the time required for disassembly and drying.
【図1】全体構成図である。FIG. 1 is an overall configuration diagram.
1:処理炉本体 2:サブバーナ 3:発酵槽 5:攪
拌翼 6:モータ(駆動機構) 15:脱臭炉 16:
バーナ 17:導入路 23:排気路 25:冷却フア
ン 29:還流路1: Processing furnace main body 2: Sub burner 3: Fermenter 5: Stirring blade 6: Motor (driving mechanism) 15: Deodorizing furnace 16:
Burner 17: Introduction path 23: Exhaust path 25: Cooling fan 29: Reflux path
Claims (3)
構により回転する攪拌翼を備えた発酵槽と、内部の空気
を加熱するバーナを備えた脱臭炉と、該脱臭炉内の空気
を前記処理炉本体内の前記発酵槽よりも下方空間に導入
する導入路と、前記発酵槽内の空気を前記脱臭炉内に還
流させる還流路と、前記脱臭炉内の空気を外部に排出さ
せる排気路とから構成されていることを特徴とする生ゴ
ミ処理装置。1. A fermenter provided with a stirring blade inside a processing furnace main body, which is rotated by a drive mechanism, a deodorizing furnace equipped with a burner for heating internal air, and an air inside the deodorizing furnace. An introduction path for introducing into the space below the fermentation tank in the processing furnace main body, a reflux path for returning air in the fermentation tank to the deodorizing furnace, and an exhaust for discharging air in the deodorizing furnace to the outside. A garbage processing device, characterized by being configured with a road.
下から加熱するサブバーナを設けたことを特徴とする請
求項1に記載の生ゴミ処理装置。2. The garbage processing device according to claim 1, further comprising a sub-burner for heating the fermentation tank from below in the processing furnace body.
冷却フアンを設けたことを特徴とする請求項1または請
求項2に記載の生ゴミ処理装置。3. The garbage treatment device according to claim 1, further comprising a cooling fan for blowing a low-temperature air flow into the exhaust passage.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5107700A JPH06292875A (en) | 1993-04-09 | 1993-04-09 | Garbage processing equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5107700A JPH06292875A (en) | 1993-04-09 | 1993-04-09 | Garbage processing equipment |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH06292875A true JPH06292875A (en) | 1994-10-21 |
Family
ID=14465740
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP5107700A Pending JPH06292875A (en) | 1993-04-09 | 1993-04-09 | Garbage processing equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH06292875A (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100334957B1 (en) * | 2000-03-13 | 2002-05-04 | 김평길 | A dry apparatus for foods waste |
| KR100343397B1 (en) * | 2000-03-13 | 2002-07-11 | 김평길 | Deodorizing apparatus of Dry machine for food wastes |
| KR100361993B1 (en) * | 2000-03-30 | 2002-11-23 | 전광수 | Dry-Fermentation apparatus |
| KR100381706B1 (en) * | 2000-10-31 | 2003-04-26 | 주식회사 가이아 | System for treating wastes |
| KR100454876B1 (en) * | 2001-06-20 | 2004-11-03 | 주식회사 가이아 | System for treating food wastes |
| KR100724686B1 (en) * | 2005-11-08 | 2007-06-08 | 정암환경(주) | Closed Circulation Type Drying Apparatus |
-
1993
- 1993-04-09 JP JP5107700A patent/JPH06292875A/en active Pending
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100334957B1 (en) * | 2000-03-13 | 2002-05-04 | 김평길 | A dry apparatus for foods waste |
| KR100343397B1 (en) * | 2000-03-13 | 2002-07-11 | 김평길 | Deodorizing apparatus of Dry machine for food wastes |
| KR100361993B1 (en) * | 2000-03-30 | 2002-11-23 | 전광수 | Dry-Fermentation apparatus |
| KR100381706B1 (en) * | 2000-10-31 | 2003-04-26 | 주식회사 가이아 | System for treating wastes |
| KR100454876B1 (en) * | 2001-06-20 | 2004-11-03 | 주식회사 가이아 | System for treating food wastes |
| KR100724686B1 (en) * | 2005-11-08 | 2007-06-08 | 정암환경(주) | Closed Circulation Type Drying Apparatus |
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