JPH09285776A - Organic waste treating device - Google Patents
Organic waste treating deviceInfo
- Publication number
- JPH09285776A JPH09285776A JP8100029A JP10002996A JPH09285776A JP H09285776 A JPH09285776 A JP H09285776A JP 8100029 A JP8100029 A JP 8100029A JP 10002996 A JP10002996 A JP 10002996A JP H09285776 A JPH09285776 A JP H09285776A
- Authority
- JP
- Japan
- Prior art keywords
- air
- tank
- heat exchange
- treatment tank
- waste
- 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.)
- Granted
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
Landscapes
- Drying Of Solid Materials (AREA)
- Processing Of Solid Wastes (AREA)
- Drying Of Gases (AREA)
- Fertilizers (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は有機廃棄物の処理装
置に係り、とくに厨芥(生ごみ)、食品製造廃棄物、バ
イオマスなど有機物全般を好気性微生物で発酵処理する
もので、一般の家庭用をはじめ、レストランや給食セン
ター等の業務用として広く適用できる有機廃棄物処理装
置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for treating organic wastes, and in particular, it is used for fermenting all organic matters such as garbage (food waste), food manufacturing wastes, biomass, etc. with aerobic microorganisms. In addition, the present invention relates to an organic waste treatment device which can be widely applied for commercial purposes such as restaurants and lunch centers.
【0002】[0002]
【従来の技術】近年、有機廃棄物を好気性微生物で発酵
処理、すなわち堆肥化(コンポスト化)する技術は、無
公害であることは勿論のこと、有機廃棄物の再利用技術
および自然還元を可能にする技術として、見直されてき
ている。特に厨芥いわゆる生ごみについては、外食産業
の拡大と食料品の多量消費に伴い、高速かつ高分解率で
発酵処理できる装置の開発が望まれてきている。従来よ
り農産廃棄物や下水汚泥などの有機物のコンポスト化
は、大部分が積極的に発酵を促進させるような手段を用
いず、長期間野積みの状態を維持することによって自然
に発酵させる方式で行われてきた。2. Description of the Related Art In recent years, the technique of fermenting organic waste with aerobic microorganisms, that is, the technique of composting (composting), is not only pollution-free, but also the recycling technique of organic waste and the natural reduction. It has been reviewed as a enabling technology. Particularly for kitchen garbage, so-called food waste, it has been desired to develop an apparatus capable of performing a fermentation process at a high speed and a high decomposition rate as the food service industry expands and a large amount of food is consumed. Traditionally, most organic composting such as agricultural waste and sewage sludge has been carried out by a method of naturally fermenting by keeping the piles open for a long time without using any means that actively promotes fermentation. I've been told.
【0003】それに対して、温度を管理し、機械的に撹
拌することによって酸素を供給するなどして発酵を促進
させ、高速で発酵処理する装置が、例えば特開平6−3
04542号公報,特開平7−124538号公報,特
開平2−229587号公報,特開平1−145388
号公報などに開示されている。On the other hand, an apparatus for controlling the temperature and mechanically stirring to supply oxygen to accelerate fermentation and to perform fermentation processing at a high speed is disclosed in, for example, Japanese Patent Laid-Open No. 6-3.
No. 04542, Japanese Patent Application Laid-Open No. 7-124538, Japanese Patent Application Laid-Open No. 2-229587, Japanese Patent Application Laid-Open No. 1-145388.
It is disclosed in Japanese Patent Publication No.
【0004】図6に示す従来の処理装置の一例により装
置の構成を説明する。処理槽10は仕切板11によっ
て、投入口2側の処理槽Aと排出口4側の処理槽Bとに
区画されている。処理槽10内には好気性微生物を培養
した基材20が蓄えられており、常に撹拌棒12,撹拌
軸8,動力伝達機構13,モータ14等で構成された撹
拌装置によって撹拌されている。ここで投入口2から処
理槽10に投入された処理物は、基材20と撹拌混合さ
れ、発酵分解が始まる。この時発酵分解による熱で処理
槽10内の温度が上昇し、有機物の発酵分解によって水
蒸気や炭酸ガスが発生する。また図6には図示していな
いが、発酵分解を促進するために処理槽10の外周を加
熱手段によって加熱している。The construction of the conventional processing apparatus shown in FIG. 6 will be described below. The processing tank 10 is divided by a partition plate 11 into a processing tank A on the input port 2 side and a processing tank B on the discharge port 4 side. A base material 20 in which aerobic microorganisms are cultured is stored in the treatment tank 10, and is constantly stirred by a stirring device including a stirring rod 12, a stirring shaft 8, a power transmission mechanism 13, a motor 14, and the like. Here, the processed material charged into the processing tank 10 through the charging port 2 is agitated and mixed with the base material 20 to start fermentation decomposition. At this time, the heat in the fermentation decomposition raises the temperature in the treatment tank 10, and the steam and carbon dioxide are generated by the fermentation decomposition of the organic matter. Although not shown in FIG. 6, the outer circumference of the treatment tank 10 is heated by a heating means in order to promote fermentation decomposition.
【0005】この水蒸気は循環ファン30によって熱交
換器35と処理槽10との間を循環しているが、熱交換
器35を通るとき冷却フアン31で冷却されるために、
水蒸気は凝縮して水滴となる。しかしこの凝縮した水は
処理物中の有機酸などにより酸性傾向となるために中和
手段36で中和される。また、さらに微生物の生息する
浄化手段37で凝縮水中に溶け込んでいる有機物を分解
された後、凝縮水は配水管38から機外に排水される。
また、炭酸ガスや臭気は熱交換器35の出口側からブロ
ア33によって吸引され、脱臭槽34に送られる。そこ
で臭気成分は脱臭槽34内の水に溶け込み、バクテリア
によって分解され、炭酸ガスは排気管39から機外に排
出されるよう構成されている。The water vapor is circulated between the heat exchanger 35 and the processing tank 10 by the circulation fan 30, but is cooled by the cooling fan 31 when passing through the heat exchanger 35.
The water vapor condenses into water droplets. However, this condensed water is neutralized by the neutralizing means 36 because it tends to be acidic due to the organic acid in the treated material. Further, after the organic matter dissolved in the condensed water is decomposed by the purification means 37 in which the microorganisms inhabit, the condensed water is discharged from the water distribution pipe 38 to the outside of the machine.
Further, carbon dioxide gas and odor are sucked by the blower 33 from the outlet side of the heat exchanger 35 and sent to the deodorizing tank 34. Therefore, the odor component is dissolved in the water in the deodorizing tank 34, decomposed by bacteria, and the carbon dioxide gas is discharged from the exhaust pipe 39 to the outside of the machine.
【0006】このようにして処理槽A内の処理物は徐々
に発酵分解され、水分が除去されてゆく。そして、比較
的軽くなった細かい粒子となった処理物は槽の上方へ浮
上し、仕切板11を溢流して排出口4側の処理槽Bに移
動する。処理槽B内でもさらに発酵分解・水分蒸発が進
行するため、処理槽A内より処理槽B内の方が処理物の
コンポスト化が進み、水分含有率も低下した状態で処理
物は、排出口4からストッカー32へ排出されるよう構
成されている。In this way, the processed material in the processing tank A is gradually fermented and decomposed to remove water. Then, the processed material, which has become relatively fine and becomes fine particles, floats above the tank, overflows the partition plate 11, and moves to the processing tank B on the discharge port 4 side. Fermentative decomposition and water evaporation further progress in the treatment tank B, so that the treatment material in the treatment tank B is more composted in the treatment tank A than in the treatment tank A, and the treatment material is discharged from the discharge port in a state in which the water content rate is lowered. 4 is discharged to the stocker 32.
【0007】[0007]
【発明が解決しようとする課題】従来の処理装置におい
ては、特開平7−124538号公報や特開平2−22
9587号公報に示されるように、高水分率の厨芥、い
わゆる生ごみを発酵に適した水分含有率(30%〜60
%)まで迅速に低下させるために、処理槽内の湿った空
気を処理槽と熱交換手段の間を循環させながら、除湿・
乾燥を行っている。この発酵分解が次第に進んで細粒
化,微粉末化した廃棄物は乾燥して軽くなり、撹拌によ
って処理槽の上部に浮上する。そして、処理槽と熱交換
手段の間を循環する空気と共に、処理槽内を浮遊し、処
理槽吸込口のフィルターの網目を閉塞する不都合が発生
した。また、循環経路においては風路の断面積や方向が
急激に変化するところの吹き溜りに堆積して、徐々に風
路を閉塞してしまった。その結果、次第に生ごみ処理装
置の除湿・乾燥機能が失われることになってしまった。
特に厨芥中に空気を圧送する方式の場合は、空気中に微
粉末が舞上がりやすく、風路の閉塞を発生しやすかっ
た。そして、除湿・乾燥機能が失われたところに、高水
分の処理物が投入されると処理槽内の汚泥化が起こり、
発酵分解が阻害され、悪臭の発生を招くことになった。In the conventional processing apparatus, Japanese Patent Application Laid-Open Nos. 7-124538 and 2-22 are used.
As shown in Japanese Patent No. 9587, a water content (30% to 60%) suitable for fermenting kitchen waste having a high water content, so-called garbage.
%) In order to quickly reduce the moisture content in the treatment tank while circulating it between the treatment tank and the heat exchange means.
It is drying. This fermentation decomposition progresses gradually, and the finely pulverized and finely divided waste is dried and becomes lighter, and floats to the upper part of the treatment tank by stirring. Then, with the air circulated between the processing tank and the heat exchange means, there was a problem that the air floated inside the processing tank and blocked the mesh of the filter of the processing tank suction port. Further, in the circulation path, the air passage accumulates in the blowhole where the cross-sectional area and the direction of the air passage change rapidly, and gradually closes the air passage. As a result, the dehumidifying / drying function of the food waste processing device was gradually lost.
In particular, in the case of a method in which air is fed under pressure into the kitchen waste, fine powder easily floats up in the air, and the air passage is easily blocked. Then, when the dehumidifying / drying function is lost, when a high-moisture treated material is added, sludge formation in the treatment tank occurs,
Fermentative decomposition was hindered, resulting in the generation of malodor.
【0008】また発酵分解に必要な空気(酸素)の供給
は、ブロアを用いて処理槽内の空気を吸引し、脱臭排気
することで槽内を負圧とし、排出口や投入口の隙間など
から外気を槽内に補充するように構成している。このと
き、処理槽内または熱交換器内の空気の温度及び湿度が
外気より高いため、ブロアに至るまでの配管が外気に触
れて冷却されると、排気される空気中の蒸気が凝縮して
配管内に溜り、溜っている水は風圧でブロア内に吸引さ
れた。この凝縮した水は厨芥に含まれる有機酸等により
PH値が低いため、吸引されてブロア内に溜るとブロ
ア,ケーシング,モータ等を腐食するばかりでなく、モ
ータの絶縁不良等を起こす原因となった。さらに、この
時一緒に吸引される空気中の微粉末が、ブロアに付着し
てモータの負荷を増大させたり、軸受の摩耗を加速し、
さらにはブロアの吸音材などにしみこんで吸音効果を低
下させる原因となった。また、循環ファンにおいても、
上記と同様な現象が起こるため、生ごみ処理システムの
寿命や安全性を低下させ、メンテナンスの費用が増大す
るなどの問題があった。The air (oxygen) necessary for fermentation decomposition is supplied by sucking the air in the treatment tank using a blower and deodorizing and exhausting it to make the inside of the tank a negative pressure, such as a gap between the discharge port and the charging port. The outside air is replenished into the tank. At this time, since the temperature and humidity of the air in the processing tank or heat exchanger are higher than the outside air, when the piping leading to the blower is exposed to the outside air and cooled, the vapor in the exhausted air condenses. The water accumulated in the pipe was sucked into the blower by wind pressure. This condensed water has a low PH value due to organic acids contained in garbage, so if it is sucked and accumulated in the blower, it will not only corrode the blower, casing, motor, etc., but also cause insulation failure of the motor. It was Furthermore, the fine powder in the air that is sucked together at this time adheres to the blower, increasing the load on the motor and accelerating the wear of the bearing.
Furthermore, the sound absorbing material such as the blower is soaked in, which causes a decrease in the sound absorbing effect. Also in the circulation fan,
Since the same phenomenon as described above occurs, there are problems that the life and safety of the food waste processing system are shortened, and the maintenance cost is increased.
【0009】[0009]
【課題を解決するための手段】本発明の有機廃棄物処理
装置は、処理槽内の上部空間に熱交換手段を設け、この
熱交換手段は、液化冷媒(圧縮機・凝縮器・膨張弁を備
えたいわゆる冷凍機の高圧側で液化した冷媒)、あるい
は冷却水を循環させて槽内を冷却し、発酵処理の過程で
発生する水蒸気を槽内で凝縮して処理槽外に排水するよ
うに構成している。In the organic waste treatment apparatus of the present invention, heat exchange means is provided in the upper space of the treatment tank, and the heat exchange means is a liquefied refrigerant (compressor / condenser / expansion valve). The so-called refrigerating machine equipped with a liquefied refrigerant on the high-pressure side) or cooling water is circulated to cool the inside of the tank, and the steam generated during the fermentation process is condensed inside the tank and discharged to the outside of the processing tank. I am configuring.
【0010】このように処理槽内の水蒸気は槽内で直接
熱交換手段により凝縮させるので、従来のように処理槽
と熱交換器の間を強制的に循環させる必要がなく、循環
気流による微粉末の舞い上がりを防止させている。した
がって、フィルターの目詰りや微粉末の堆積によるダク
ト内の閉塞によって起るさまざまな問題を解決するばか
りでなく、処理槽と熱交換器の間を強制的に循環させる
手段、例えば循環ファンや熱交換器と処理槽を連結する
ダクトホース,さらには処理槽の吸引口のフィルター等
が不要となり、装置の小型化を図ることができる。As described above, since the water vapor in the treatment tank is directly condensed in the tank by the heat exchange means, it is not necessary to forcibly circulate the water vapor between the treatment tank and the heat exchanger as in the conventional case. It prevents the powder from rising. Therefore, it not only solves various problems caused by clogging of the filter and blockage of the duct due to accumulation of fine powder, but also means for forcibly circulating between the processing tank and the heat exchanger, such as a circulation fan or a heat exchanger. The duct hose connecting the exchanger and the processing tank, and the filter of the suction port of the processing tank are not required, and the apparatus can be downsized.
【0011】さらに、本発明の有機廃棄物処理装置は、
処理槽上部に処理槽内部に連絡する空間を有する熱交換
室を設け、処理槽内で発生した温度の高い水蒸気を第2
の開口部を通して熱交換室に導入し、熱交換室内に配設
する熱交換手段により凝縮させる。この凝縮した水は熱
交換室からドレン樋等に導水され機外に排水される。Further, the organic waste treatment apparatus of the present invention is
A heat exchange chamber having a space communicating with the inside of the processing tank is provided above the processing tank, and the high temperature steam generated in the processing tank is second
Is introduced into the heat exchange chamber through the opening and is condensed by the heat exchange means arranged in the heat exchange chamber. The condensed water is introduced from the heat exchange chamber to a drain gutter or the like and discharged outside the machine.
【0012】また、本発明の有機廃棄物処理装置は、好
気発酵処理に必要な空気を循環させる酸素供給手段を、
処理槽や熱交換室の上部に気液分離器を介して連絡して
配設し、取り出した処理槽の空気を外気に接触させて熱
交換させることにより、外気温度における飽和蒸気とさ
せ、その後、気液分離器に導入した凝縮した水を分離し
て中和槽へ導くと共に、気液分離器から送出される空気
を処理槽の外壁や内壁に接触させることにより、再熱さ
れ乾燥空気として酸素供給手段に流入させる。したがっ
て酸素供給手段は十分乾燥された空気を吸引することに
なり、凝縮水を含んだ空気によるケーシングの腐食やモ
ータの絶縁不良、さらには吸音材の吸湿による騒音発生
などの問題は解消される。Further, the organic waste treatment apparatus of the present invention comprises an oxygen supply means for circulating the air necessary for the aerobic fermentation treatment,
It is placed in communication with the upper part of the treatment tank or heat exchange chamber via a gas-liquid separator, and the taken-out air from the treatment tank is brought into contact with the outside air to cause heat exchange, thereby making it a saturated vapor at the outside air temperature, and thereafter. , The condensed water introduced into the gas-liquid separator is separated and guided to the neutralization tank, and the air sent from the gas-liquid separator is brought into contact with the outer wall and the inner wall of the processing tank to be reheated to produce dry air. Flow into the oxygen supply means. Therefore, the oxygen supply means sucks sufficiently dried air, and the problems such as the corrosion of the casing due to the air containing condensed water, the insulation failure of the motor, and the noise generation due to the moisture absorption of the sound absorbing material are solved.
【0013】[0013]
【発明の実施の形態】以下、本発明の実施例を図面によ
り説明する。 〔実施例1〕図1および図2において実施例1を説明す
る。図1は本発明の処理槽内に設けた熱交換器を有する
廃棄物処理装置の構造説明図である。処理槽50の上部
には投入口52が開口され、投入口52は蓋54で閉塞
されている。また、処理槽50の底部は断面が半円形を
二つ並列に連結した略ギリシャ文字の「ω」形状をして
いる。処理槽50の外壁には温水パイプ53が蛇行して
複数本配設されており、温水器などから供給される温水
を温水パイプ53内に循環させることにより、処理槽5
0の底部を加熱している。この加熱手段により処理槽5
0内の処理物は発酵に適した温度50℃〜80℃に保持
される。また、仕切板55は図2に示す如く処理槽50
を投入口52側の処理槽Aと、排出口57側の処理槽B
に区画するように配設される。仕切板55は処理物が処
理槽Aから処理槽Bに溢流できる高さに設定されてい
る。Embodiments of the present invention will be described below with reference to the drawings. [Embodiment 1] Embodiment 1 will be described with reference to FIGS. FIG. 1 is a structural explanatory view of a waste treatment device having a heat exchanger provided in the treatment tank of the present invention. An input port 52 is opened at the top of the processing tank 50, and the input port 52 is closed by a lid 54. In addition, the bottom of the processing tank 50 has a substantially Greek letter “ω” shape in which two semicircular sections are connected in parallel. A plurality of hot water pipes 53 are arranged in a meandering manner on the outer wall of the treatment tank 50. By circulating hot water supplied from a water heater or the like in the hot water pipe 53, the treatment tank 5
The bottom of 0 is heating. By this heating means, the processing tank 5
The treated material in 0 is maintained at a temperature suitable for fermentation of 50 ° C to 80 ° C. Further, the partition plate 55 is the processing tank 50 as shown in FIG.
Processing tank A on the inlet 52 side and processing tank B on the outlet 57 side
It is arranged so as to be divided into. The partition plate 55 is set to such a height that the processed material can overflow from the processing tank A to the processing tank B.
【0014】処理槽50の底部を形成する半円形状の中
心位置には、撹拌軸61A,62A,61B,62Bを
配設する。それぞれの撹拌軸には、撹拌棒65が放射状
に複数本固定されている。撹拌棒65は撹拌軸61
(A,B)、62(A,B)の周面に適宜角度をもって
螺旋状に植設されている。したがって、撹拌軸61
(A,B)、62(A,B)が回転すると処理槽内の基
材や処理物はその回転によって生じる撹拌棒65による
搬送力で、投入口52側、もしくは排出口57側へと槽
内で移動する。さらに、仕切板55の中央には連通口5
50を設け、上記搬送力によって処理物が連通口550
を通って処理槽Aと処理槽Bとの間を往来する構成とな
っている。特に処理槽A内に高水分の生ごみが多量に投
入されたときは、汚泥化が起り水分の蒸発を阻害する
が、乾燥した処理物が処理槽Bから連通口550を通っ
て処理槽Aへ逆流するように撹拌軸の回転を制御するこ
とにより、迅速に処理槽A内の水分調整が実行され、汚
泥化することなく効果的に処理槽50内に蒸気を蒸散す
ることができるものである。Agitating shafts 61A, 62A, 61B and 62B are arranged at the central positions of the semicircular shapes forming the bottom of the processing tank 50. A plurality of stirring rods 65 are radially fixed to each stirring shaft. The stirring rod 65 is the stirring shaft 61.
(A, B) and 62 (A, B) are spirally planted at an appropriate angle on the peripheral surface. Therefore, the stirring shaft 61
When (A, B) and 62 (A, B) rotate, the substrate and the processed material in the processing tank are transferred to the inlet 52 side or the outlet 57 side by the conveying force of the stirring rod 65 generated by the rotation. Move in. Further, the communication port 5 is provided at the center of the partition plate 55.
50 is provided, and the processed product is communicated with the communication port 550 by the above-described conveying force
It is configured to pass back and forth between the processing tank A and the processing tank B through the passage. In particular, when a large amount of high-moisture garbage is put into the treatment tank A, sludge formation occurs and water evaporation is hindered, but the dried treated material passes from the treatment tank B through the communication port 550 to the treatment tank A. By controlling the rotation of the stirring shaft so as to flow back into the treatment tank A, the water content in the treatment tank A can be quickly adjusted, and the vapor can be effectively evaporated into the treatment tank 50 without turning it into sludge. is there.
【0015】処理槽50内上部空間には熱交換器70と
ドレン樋75が設けられている。ドレン樋75は滴下し
た凝縮水が処理槽50内の熱気によって再蒸発しないよ
うに断熱性を有している。熱交換器70は冷凍機の蒸発
器を用いたり、冷却水を循環したりして、処理槽50内
の空気より低温に保たれている。A heat exchanger 70 and a drain gutter 75 are provided in the upper space of the processing tank 50. The drain gutter 75 has a heat insulating property so that the dropped condensed water is not re-evaporated by the hot air in the treatment tank 50. The heat exchanger 70 is kept at a temperature lower than that of the air in the processing tank 50 by using an evaporator of a refrigerator or circulating cooling water.
【0016】図1に示す実施例では熱交換器70は、処
理槽50の天板51上に配設する圧縮機71,凝縮器7
2,冷却ファン73等とともに冷凍サイクルを構成し、
蒸発機能を有している。したがって処理槽50の上部空
間に蒸散した水蒸気は、熱交換器70で冷却されるため
に、その表面に凝縮し水滴となってドレン樋75に滴下
する。この水蒸気は有機物が溶け込んでいるばかりでな
く、有機廃棄物の発酵処理過程で生成される有機酸など
によりPH値が低くなっている。そこで、ドレン樋75
から中和槽74に導水して調整する。さらに水に溶け込
んでいる有機物は脱臭槽76内に生息するバクテリアで
分解され、排水管77を経由して機外に排出される。ま
た、熱交換器70が水蒸気から受け取った熱は、冷凍サ
イクルの冷媒によって槽外に設けられた凝縮器72に運
ばれ、圧縮機71が消費した電気エネルギーと共に、冷
却ファン73により機外に放出される。In the embodiment shown in FIG. 1, the heat exchanger 70 comprises a compressor 71 and a condenser 7 arranged on the top plate 51 of the processing tank 50.
2, constitutes a refrigeration cycle together with the cooling fan 73,
It has an evaporation function. Therefore, the water vapor evaporated in the upper space of the processing tank 50 is cooled by the heat exchanger 70, so that it is condensed on the surface thereof and becomes a water drop and is dropped on the drain gutter 75. Not only the organic matter is dissolved in this water vapor, but also the PH value is lowered due to the organic acid produced in the fermentation treatment process of the organic waste. So drain gutter 75
From the water to the neutralization tank 74 for adjustment. Further, the organic matter dissolved in the water is decomposed by the bacteria living in the deodorization tank 76, and is discharged to the outside of the machine through the drain pipe 77. Further, the heat received from the steam by the heat exchanger 70 is carried to the condenser 72 provided outside the tank by the refrigerant of the refrigeration cycle, and is discharged outside the machine by the cooling fan 73 together with the electric energy consumed by the compressor 71. To be done.
【0017】以上の如く熱交換手段を処理槽内に設ける
この処理装置は、有機廃棄物中の水分を、温水パイプな
どで加熱して蒸発させ、撹拌手段で効果的に撹拌しなが
ら処理槽上部空間へ蒸散させ、その水蒸気を自然対流に
よって熱交換器に導き、水分を除去するものである。As described above, this processing apparatus, in which the heat exchange means is provided in the processing tank, heats the water in the organic waste by a hot water pipe or the like to evaporate it, and the stirring means effectively agitates the upper portion of the processing tank. It evaporates into the space, and the water vapor is guided to the heat exchanger by natural convection to remove water.
【0018】次に発酵分解に必要な酸素の供給系統につ
いて説明する。処理槽50の天板51を貫通する第1の
排気管80を設ける。第1の排気管80の一端は処理槽
50空間に開口し、他端は凝縮器72に隣接する気液分
離器81に接続されている。排気管80は凝縮器72と
気液分離器81との間で蛇行させて配設している。この
ように構成することにより、吸込グリル83から冷却フ
ァン73によって吸引される外気を排気管80に当てて
排気管80内に吸い込まれた処理槽50内の高湿度の空
気を冷却する。この構成により、処理槽50内の高湿度
の空気は気液分離器81を通過する前に、第1の排気管
80内において水蒸気を凝縮させることができる。排気
管80内で凝縮した水は気液分離器81に溜り、ドレン
パイプ84から中和槽74へ排出される。Next, the supply system of oxygen required for fermentation decomposition will be described. A first exhaust pipe 80 that penetrates the top plate 51 of the processing tank 50 is provided. One end of the first exhaust pipe 80 opens into the space of the processing tank 50, and the other end is connected to the gas-liquid separator 81 adjacent to the condenser 72. The exhaust pipe 80 is arranged in a meandering manner between the condenser 72 and the gas-liquid separator 81. With this configuration, the outside air sucked by the cooling fan 73 from the suction grill 83 is applied to the exhaust pipe 80 to cool the high-humidity air in the processing tank 50 sucked into the exhaust pipe 80. With this configuration, the high-humidity air in the processing tank 50 can condense water vapor in the first exhaust pipe 80 before passing through the gas-liquid separator 81. The water condensed in the exhaust pipe 80 accumulates in the gas-liquid separator 81 and is discharged from the drain pipe 84 to the neutralization tank 74.
【0019】一方、水蒸気が除去された気液分離器81
内の空気は、気液分離器81の上部に連設する第2の排
気管85に入る。第2の排気管85は処理槽50の外
壁、もしくは内壁に接触するように配設され、ブロア8
6の吸込口89に連結されている。処理槽50は50℃
〜80℃にたもたれているので、第2の排気管85は処
理槽50の壁に接触することによって再び加熱される。
そして、第2の排気管85内の空気は加熱されて乾燥空
気となってからブロア86に入ることになる。したがっ
て、ブロア86に吸引される第2の排気管85内の空気
は、管内通過途上に水蒸気が凝縮することがない。その
結果、ブロア86のケーシング内に水分が吸入されるこ
ともないので、水分吸入によるブロア86のトラブルが
解消される。この第2の排気管の再熱に電熱ヒータを用
いても同様の効果が得られる。On the other hand, the gas-liquid separator 81 from which water vapor has been removed
The air inside enters the second exhaust pipe 85 that is connected to the upper portion of the gas-liquid separator 81. The second exhaust pipe 85 is disposed so as to come into contact with the outer wall or the inner wall of the processing tank 50, and the blower 8
6 is connected to the suction port 89. Treatment tank 50 is 50 ° C
Since it is leaning at -80 ° C, the second exhaust pipe 85 is heated again by coming into contact with the wall of the processing tank 50.
Then, the air in the second exhaust pipe 85 is heated to become dry air and then enters the blower 86. Therefore, in the air in the second exhaust pipe 85 sucked by the blower 86, the water vapor does not condense while passing through the pipe. As a result, water is not sucked into the casing of the blower 86, so that the trouble of the blower 86 due to the suction of water is eliminated. The same effect can be obtained by using an electric heater for reheating the second exhaust pipe.
【0020】また、処理槽50内の上部空間に設置され
る熱交換器70は水平面に対して角度αを7度以上の角
度をもって取り付けてある。熱交換器70の傾斜した配
設により、水滴は熱交換器70の下端に達したとき、表
面張力によって懸垂しながらその傾斜に添って流れ、ド
レン樋75に集められて排水される。The heat exchanger 70 installed in the upper space of the processing tank 50 is attached at an angle α of 7 degrees or more with respect to the horizontal plane. Due to the inclined arrangement of the heat exchanger 70, when the water drop reaches the lower end of the heat exchanger 70, the water drops flow along the inclination while being suspended by the surface tension, and are collected in the drain gutter 75 and drained.
【0021】〔実施例2〕次に処理装置の他の実施例を
説明する(図3,図4,図5参照)。なお、実施例1と
同様の構成、および作用をなす部材には同一の符号を付
してその説明を省略している。処理槽50の廃棄物投入
口52に隣接して開口部530を設け、開口部530の
上部に熱交換室150を配設する。熱交換室150は熱
交換器200が複数個設置されている。[Second Embodiment] Next, another embodiment of the processing apparatus will be described (see FIGS. 3, 4 and 5). It should be noted that members having the same configurations and functions as those of the first embodiment are designated by the same reference numerals and the description thereof is omitted. An opening 530 is provided adjacent to the waste input port 52 of the processing tank 50, and the heat exchange chamber 150 is provided above the opening 530. A plurality of heat exchangers 200 are installed in the heat exchange chamber 150.
【0022】熱交換器200の構成を図5により説明す
る。平板210の対向する両端を折り曲げて折曲片21
1を形成した伝熱板200Aを形成する。折曲片211
の折り曲げ方向と反対側の伝熱板200Aの面に、シー
ル材を塗布したスペーサ215を介在させて、第2の伝
熱板200Aを配設する。このとき、隣接する伝熱板2
00Aの折曲片211は互いに直交する位置となるよう
に配設する。このように複数枚の伝熱板200Aを交互
に90°向きを変えて並設して一つの熱交換器200を
形成する。このように構成する熱交換器200は隣接す
る伝熱板200Aの間に、矢印X方向に形成される槽内
空気の風路となる第1の風路220と、第1の風路22
0に直交する矢印Y方向に形成される外気の風路となる
第2の風路230が形成される。熱交換器200は第1
の風路220を通過する開口部530からの水蒸気を含
んだ温度の高い処理槽50内からの空気と、第2の風路
230を通過する外気が、伝熱板200Aを介して直交
する流れを形成し、伝熱板200Aの両面で効果的に熱
交換される。このとき、伝熱板200Aに放熱フィン2
50を設けることにより熱交換効率の向上が図れる。放
熱フイン250は伝熱板200Aのスペーサ215に平
行して複数配設される。The structure of the heat exchanger 200 will be described with reference to FIG. Bend pieces 21 by bending the opposite ends of the flat plate 210.
The heat transfer plate 200A on which No. 1 is formed is formed. Bent piece 211
The second heat transfer plate 200A is arranged on the surface of the heat transfer plate 200A on the side opposite to the bending direction, with a spacer 215 coated with a sealing material interposed. At this time, the adjacent heat transfer plate 2
The bent pieces 211 of 00A are arranged at positions orthogonal to each other. In this way, a plurality of heat transfer plates 200A are alternately arranged side by side with their directions changed by 90 ° to form one heat exchanger 200. In the heat exchanger 200 configured in this manner, the first air passage 220 and the first air passage 22 which are air passages for the in-tank air formed in the arrow X direction between the adjacent heat transfer plates 200A.
A second air passage 230, which is an air passage for the outside air formed in the direction of the arrow Y orthogonal to 0, is formed. Heat exchanger 200 is the first
The air from the inside of the high-temperature treatment tank 50 containing water vapor from the opening 530 passing through the air passage 220 and the outside air passing through the second air passage 230 flow at right angles through the heat transfer plate 200A. And heat is effectively exchanged on both sides of the heat transfer plate 200A. At this time, the radiation fins 2 are attached to the heat transfer plate 200A.
By providing 50, the heat exchange efficiency can be improved. A plurality of heat radiation fins 250 are arranged in parallel with the spacers 215 of the heat transfer plate 200A.
【0023】また、熱交換器200と筐体260との間
隙は処理槽50に通ずる風路240となる。そこで、処
理槽50内の水蒸気を含んだ空気は、風路240を通過
して処理装置の上部に上昇し、熱交換室150の上部空
間に達する。一方、熱交換器200を通過途上、伝熱板
200Aに接触した空気は、熱交換されて冷却される。
このとき、処理槽50内の空気に含まれる水蒸気は凝縮
して伝熱板200Aに結露する。そして、冷却されて重
くなった空気は自然に重力で下方(処理槽方向)へ流下
する。その流れにしたがって風路240から熱交換室1
50の上部に達した空気は、熱交換器200内に吸引さ
れる。ここで、冷却ファン73を始動させるとグリル8
3から外気を吸引する。この吸引された外気は熱交換器
200内の第2の風路230を水平方向(矢印Y方向)
に流下する。外気は第2の風路230を通過途上、伝熱
板200Aから熱を奪い、機外に放出される。The gap between the heat exchanger 200 and the housing 260 serves as an air passage 240 communicating with the processing tank 50. Therefore, the air containing water vapor in the processing tank 50 passes through the air passage 240, rises to the upper part of the processing device, and reaches the upper space of the heat exchange chamber 150. On the other hand, the air that has contacted the heat transfer plate 200A while passing through the heat exchanger 200 is heat-exchanged and cooled.
At this time, the water vapor contained in the air in the processing tank 50 is condensed and condensed on the heat transfer plate 200A. Then, the cooled and heavy air naturally flows downward by gravity due to gravity. According to the flow, from the air passage 240 to the heat exchange chamber 1
The air reaching the upper part of 50 is sucked into the heat exchanger 200. Here, when the cooling fan 73 is started, the grill 8
Aspirate outside air from 3. The sucked outside air flows in the second air passage 230 in the heat exchanger 200 in the horizontal direction (arrow Y direction).
Flow down to The outside air takes heat from the heat transfer plate 200A while passing through the second air passage 230 and is discharged to the outside of the machine.
【0024】このように、この実施例に示す処理装置は
実施例1と同様に強制的に処理槽50内の空気を循環さ
せることがないので、処理槽50内に乾燥した微粉末を
舞い上げることなく発酵処理過程で発生した水蒸気を除
去する。以上説明した処理槽内に設ける熱交換器は、実
施例1に示す熱交換器70は冷凍機の蒸発器を用いた
り、水を循環して冷却するのに好都合な構造であり、実
施例2に示す熱交換器は外気で冷却するのに好都合な構
造となっている。また、この実施例に示す熱交換室15
0内に設置した熱交換器200は下端の面の傾きが水平
面に対して角度βを7度以上の角度をもって配設され
る。この傾斜した配設により水滴は熱交換器200の下
端に達したとき、表面張力によって懸垂しながらその傾
斜に添って流れ、ドレン樋750に集められ、実施例1
で説明した経路で排水される。As described above, since the processing apparatus shown in this embodiment does not forcibly circulate the air in the processing tank 50 as in the case of the first embodiment, the dry fine powder is flown into the processing tank 50. Without removing the steam generated in the fermentation process. The heat exchanger provided in the processing tank described above has a structure that is convenient for the heat exchanger 70 shown in the first embodiment to use the evaporator of the refrigerator or to circulate and cool the water. The heat exchanger shown in (1) has a structure that is convenient for cooling with outside air. In addition, the heat exchange chamber 15 shown in this embodiment
The heat exchanger 200 installed in 0 is disposed such that the inclination of the lower end surface is an angle β of 7 degrees or more with respect to the horizontal plane. When the water droplets reach the lower end of the heat exchanger 200 by this inclined arrangement, the water droplets are suspended by the surface tension and flow along the inclination, and are collected in the drain gutter 750.
It will be drained through the route described in.
【0025】また、図5に示すように、伝熱板200A
の折曲部211に水滴の流れるU字または凹凸の溝21
2を設けることにより、さらに確実に効率良く水滴をド
レン樋75に集めることができるものである。したがっ
て、熱交換器200の下端の面を水平に取り付けた場
合、または取付け傾斜が少ない(7度以下)場合には、
水滴は途中で適下して熱交換器200の一方に集めるこ
とができず、伝熱板200Aの全巾にわたってドレン樋
を配設する必要があるが、この実施例のドレン樋750
は傾斜した熱交換器200の最下部に滴下する水滴が集
められる範囲の小さな樋でよい。自然対流による処理槽
内空気の循環を利用した除湿方式において大きな面積の
樋は上昇する空気の流れを阻害するものであり、ドレン
樋の巾は狭い方がこのましいことは記述するまでもない
ことである。Further, as shown in FIG. 5, the heat transfer plate 200A
U-shaped or concave / convex groove 21 in which water drops flow in the bent portion 211 of the
By providing 2, the water droplets can be more reliably and efficiently collected in the drain gutter 75. Therefore, when the lower end surface of the heat exchanger 200 is mounted horizontally, or when the mounting inclination is small (7 degrees or less),
Water drops cannot be properly collected on the way and collected in one side of the heat exchanger 200, and it is necessary to dispose a drain gutter over the entire width of the heat transfer plate 200A. However, the drain gutter 750 of this embodiment is used.
May be a small gutter in a range where water drops dripping at the bottom of the inclined heat exchanger 200 are collected. In the dehumidification method that uses the circulation of air in the treatment tank by natural convection, a large area gutter obstructs the rising air flow, and it is needless to say that a narrow drain gutter is preferable. That is.
【0026】[0026]
【発明の効果】本発明の廃棄物の処理装置は処理槽内に
熱交換手段を設けることによって、処理槽内の高温多湿
の空気を除湿用の熱交換手段に自然対流で導くもので、
これにより処理槽内の乾燥した微粉末の舞い上がりを防
止できる。したがって、従来使用していた空気循環用の
ファン,処理槽と除湿装置を連結する風路ダクトやフィ
ルターが不要になることは勿論、これらの機械的トラブ
ルが原因となって起こる処理槽内の汚泥化,悪臭の発生
が減少し、メンテナンスのための費用が軽減されるな
ど、製品の信頼性向上・製造コスト及びランニングコス
ト低減の面でその効果は大きい。また、空気(酸素)供
給用ブロアの吸引側の空気配管を外気で冷却し気液分離
し、処理槽の壁面で再熱するという簡単な方法で、ブロ
アの吸引側空気を乾燥させ、水分吸入によるブロアモー
タの絶縁不良,ケーシング等の腐食,騒音発生などのト
ラブルを防止できるものである。EFFECTS OF THE INVENTION The waste treatment apparatus of the present invention is provided with heat exchange means in the treatment tank to guide the hot and humid air in the treatment tank to the heat exchange means for dehumidification by natural convection.
As a result, it is possible to prevent the dry fine powder in the processing tank from rising. Therefore, the fan for air circulation, the air duct that connects the treatment tank and the dehumidifier, and the filter that have been used conventionally are not required, and the sludge in the treatment tank caused by these mechanical troubles is of course unnecessary. It has a great effect in terms of improving product reliability, reducing manufacturing cost and running cost, such as reduction in odor and odor, and reduction in maintenance cost. Also, the suction side of the blower for supplying air (oxygen) is cooled with outside air to separate gas and liquid, and the wall of the processing tank is reheated. It is possible to prevent problems such as poor insulation of the blower motor, corrosion of the casing, noise generation, etc.
【0027】さらに、本発明の廃棄物の処理装置は処理
槽の上に熱交換室を設けて処理槽の上面と熱交換室の下
面が連通するように配置して、処理槽内に熱交換手段を
設けたものと同様な効果を得ることによって、処理槽内
の湿り空気を除湿用の熱交換器に自然対流で導くもの
で、これにより処理槽内の乾燥した微粉末の舞い上がり
を防止できる。Further, in the waste treatment apparatus of the present invention, a heat exchange chamber is provided on the treatment tank so that the upper surface of the treatment tank and the lower surface of the heat exchange chamber communicate with each other, and heat is exchanged in the treatment tank. By obtaining the same effect as the one provided with the means, the humid air in the treatment tank is guided to the heat exchanger for dehumidification by natural convection, which prevents the dry fine powder in the treatment tank from rising up. .
【図1】本発明による有機廃棄物処理装置の構成説明断
面図。FIG. 1 is a cross-sectional view illustrating the configuration of an organic waste treatment device according to the present invention.
【図2】処理槽の平面図。FIG. 2 is a plan view of a processing tank.
【図3】本発明による有機廃棄物処理装置の構成説明断
面図。FIG. 3 is a sectional view for explaining the configuration of the organic waste treatment device according to the present invention.
【図4】熱交換室の説明斜視図。FIG. 4 is an explanatory perspective view of a heat exchange chamber.
【図5】伝熱板の形状と組合せ説明図。FIG. 5 is an explanatory view of a shape and combination of heat transfer plates.
【図6】従来の処理装置の一実施例を示す説明断面図。FIG. 6 is an explanatory sectional view showing an embodiment of a conventional processing apparatus.
50 処理槽 52 投入口 52 開口部 53 温水パイプ 55 仕切板 54 蓋 61A,B 撹拌軸 62A,B 撹拌軸 65 撹拌棒 73 冷却ファン 74 中和槽 75 750 ドレン樋 76 脱臭槽 80 排気管 81 気液分離器 86 ブロア 74 中和槽 76 脱臭槽 150 熱交換室 200 熱交換器 200A 伝熱板 215 スペーサ 220 第1の風路 230 第2の風路 50 treatment tank 52 input port 52 opening 53 hot water pipe 55 partition plate 54 lid 61A, B stirring shaft 62A, B stirring shaft 65 stirring rod 73 cooling fan 74 neutralization tank 75 750 drain gutter 76 deodorization tank 80 exhaust pipe 81 gas liquid Separator 86 Blower 74 Neutralization tank 76 Deodorization tank 150 Heat exchange chamber 200 Heat exchanger 200A Heat transfer plate 215 Spacer 220 First air passage 230 Second air passage
Claims (8)
投入された廃棄物を撹拌、搬送する撹拌搬送手段と、廃
棄物を好気発酵処理させる処理槽に配設する加熱手段
と、発酵処理過程において発生する水蒸気を凝縮させる
熱交換手段と、処理槽内の空気を乾燥させて循環させる
酸素供給手段を備え、 熱交換手段は、投入口から投入される廃棄物に干渉しな
い処理槽内上部空間位置に配設されてなる有機廃棄物処
理装置。1. A treatment tank having a port for introducing waste,
An agitating and conveying means for agitating and conveying the input waste, a heating means arranged in a treatment tank for aerobically fermenting the waste, a heat exchange means for condensing steam generated in the fermentation treatment process, and a treatment tank An organic waste treatment apparatus comprising oxygen supply means for drying and circulating the internal air, wherein the heat exchange means is arranged at an upper space position in the treatment tank that does not interfere with the waste introduced from the inlet.
ともに冷凍サイクルを形成する蒸発器よりなる請求項1
の有機廃棄物処理装置。2. The heat exchange means comprises an evaporator forming a refrigeration cycle together with a compressor, a condenser and an expansion valve.
Organic waste treatment equipment.
隣接する第2の口を天板に開口する処理槽と、投入され
た廃棄物を撹拌、搬送する撹拌搬送手段と、廃棄物を好
気発酵処理させる処理槽に配設する加熱手段と、発酵処
理過程において発生する水蒸気を凝縮させる熱交換手段
と、処理槽内の空気を乾燥させて循環させる酸素供給手
段を備え、 処理槽の第2の口には処理槽内に連通する空間を有し、
熱交換手段を配設する熱交換室を設け、熱交換室は外気
を導入する風路を形成して、処理槽内から流入する水蒸
気を含む空気を外気によって冷却させるよう構成してな
る有機廃棄物処理装置。3. A treatment tank in which a first port for introducing waste and a second port adjacent to the first port are opened in a top plate, and an agitating and conveying means for agitating and conveying the introduced waste. A heating means arranged in a treatment tank for aerobically fermenting waste, a heat exchange means for condensing water vapor generated in the fermentation treatment process, and an oxygen supply means for drying and circulating the air in the treatment tank , The second opening of the processing tank has a space communicating with the processing tank,
An organic waste which is provided with a heat exchange chamber for arranging heat exchange means, the heat exchange chamber forming an air passage for introducing the outside air, and cooling the air containing the steam flowing from the inside of the processing tank by the outside air. Material processing equipment.
路、および外気の風路を形成する並設した複数の伝熱板
を備えてなる請求項3記載の有機廃棄物処理装置。4. The organic waste treatment apparatus according to claim 3, wherein the heat exchange means comprises a plurality of heat transfer plates arranged in parallel to form an air passage for the air from the treatment tank and an air passage for the outside air.
請求項4記載の有機廃棄物処理装置。5. The organic waste treatment device according to claim 4, wherein the heat transfer plate is provided with a guide groove for condensed water.
7°以上となるよう傾斜させて配設してなる請求項1ま
たは請求項3記載の有機廃棄物処理装置。6. The organic waste treatment apparatus according to claim 1 or 3, wherein the heat exchange means is arranged so as to be inclined at an angle of 7 ° or more with the horizontal plane of the treatment tank.
器を介して酸素供給手段に流入するよう構成されてなる
請求項1または3記載の有機廃棄物処理装置。7. The organic waste treatment device according to claim 1, wherein the air in the treatment tank is cooled and then introduced into the oxygen supply means through a gas-liquid separator.
空気は処理槽の内壁または外壁に接触する経路を形成
し、加熱されるよう構成されてなる請求項7記載の有機
廃棄物処理装置。8. The organic waste treatment device according to claim 7, wherein the air flowing from the gas-liquid separator into the oxygen supply means forms a path for contacting the inner wall or the outer wall of the treatment tank and is heated. .
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10002996A JP3383150B2 (en) | 1996-04-22 | 1996-04-22 | Organic waste treatment equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP10002996A JP3383150B2 (en) | 1996-04-22 | 1996-04-22 | Organic waste treatment equipment |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH09285776A true JPH09285776A (en) | 1997-11-04 |
JP3383150B2 JP3383150B2 (en) | 2003-03-04 |
Family
ID=14263118
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP10002996A Expired - Fee Related JP3383150B2 (en) | 1996-04-22 | 1996-04-22 | Organic waste treatment equipment |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3383150B2 (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002186942A (en) * | 2000-12-22 | 2002-07-02 | Tanico Corp | Garbage disposer |
WO2002064273A1 (en) * | 2001-02-15 | 2002-08-22 | Tama-Tlo, Ltd. | Method and system for treating organic matter utilizing substance circulation system |
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CN114485080A (en) * | 2022-01-24 | 2022-05-13 | 张家界夏花仿真花有限责任公司 | Drying equipment is used in production of artificial flower |
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Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
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KR102276946B1 (en) * | 2019-12-27 | 2021-07-13 | (주)지에이 | A food waste removal apparatus |
-
1996
- 1996-04-22 JP JP10002996A patent/JP3383150B2/en not_active Expired - Fee Related
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002186942A (en) * | 2000-12-22 | 2002-07-02 | Tanico Corp | Garbage disposer |
WO2002064273A1 (en) * | 2001-02-15 | 2002-08-22 | Tama-Tlo, Ltd. | Method and system for treating organic matter utilizing substance circulation system |
CN104197667A (en) * | 2014-09-28 | 2014-12-10 | 成都冠禹科技有限公司 | Industrial compartment-type drying and crushing device |
CN111825488A (en) * | 2019-11-05 | 2020-10-27 | 江西省三余环保节能科技有限公司 | High-efficiency energy-saving fermentation treatment device |
CN111825488B (en) * | 2019-11-05 | 2024-09-13 | 江西省三余环保节能科技股份有限公司 | High-efficiency energy-saving fermentation treatment device |
CN115406199A (en) * | 2021-05-26 | 2022-11-29 | 南昌诺汇医药科技有限公司 | Detection medicament drying device and using method |
CN114378106A (en) * | 2022-01-15 | 2022-04-22 | 江西省三余环保节能科技股份有限公司 | Organic matter decomposition fermentation machine |
CN114485080A (en) * | 2022-01-24 | 2022-05-13 | 张家界夏花仿真花有限责任公司 | Drying equipment is used in production of artificial flower |
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---|---|
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