JP2003245640A - Garbage processor - Google Patents

Garbage processor

Info

Publication number
JP2003245640A
JP2003245640A JP2002049094A JP2002049094A JP2003245640A JP 2003245640 A JP2003245640 A JP 2003245640A JP 2002049094 A JP2002049094 A JP 2002049094A JP 2002049094 A JP2002049094 A JP 2002049094A JP 2003245640 A JP2003245640 A JP 2003245640A
Authority
JP
Japan
Prior art keywords
garbage
section
drying
microbial decomposition
outside air
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
Application number
JP2002049094A
Other languages
Japanese (ja)
Other versions
JP3843862B2 (en
Inventor
Katsuzo Konakawa
勝蔵 粉川
Hideo Tomita
英夫 富田
Takeshi Hatano
剛 羽田野
Masanobu Kawai
雅信 河合
Hiroshi Nishida
博史 西田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP2002049094A priority Critical patent/JP3843862B2/en
Publication of JP2003245640A publication Critical patent/JP2003245640A/en
Application granted granted Critical
Publication of JP3843862B2 publication Critical patent/JP3843862B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

<P>PROBLEM TO BE SOLVED: To provide a stable garbage treatment without deteriorating the microbial decomposition capacity of a garbage in a garbage processor. <P>SOLUTION: A constitution is so made that the garbage processor is provided with a dry treatment section 13 where the garbage is dried by sending a fresh air thereto, a first blower 18 which supplies the fresh air to the section 13, a microbial decomposition treatment section 14 and a stirring section 21 which stirs the garbage in the section 13 and the section 14. This allows an energy to be saved by drying the garbage to remove a water content by an atmospheric heat caused by a ventilation, the deterioration of a decomposition performance can be prevented by suppressing the rise of a humidity in the section 14 and further, the generation of an offensive odor is simultaneously suppressed. <P>COPYRIGHT: (C)2003,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は主に家庭で発生する
生ゴミを減量及び減容させる生ゴミ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 food waste, which mainly reduces and reduces the amount of food waste produced at home.

【0002】[0002]

【従来の技術】従来の生ごみの量を減量したり、減容し
たりする生ゴミ処理装置では、図4に示すように、微生
物の生息場所となるおがくず等の微生物担体1を入れた
微生物分解槽2と、投入された生ゴミ3と微生物担体1
とを混合、撹拌するための回転撹拌棒4及びその駆動装
置5を有し、投入された生ごみ3を微生物により最終的
には二酸化炭素と水に分解し、生ごみ3を減容減量する
もので、微生物分解槽2内の温度を適正に保つための加
熱手段6、酸素(空気)を供給するための送風装置7、
それらの制御を行う制御手段(図示せず)を備え、微生
物の働きにより生ごみを分解し減量するいわゆるバイオ
式生ごみ処理装置と、図5に示すように、加熱装置8と
送風装置9を有し、生ごみ3を底部に駆動装置10で回
転する撹拌羽根11を具備した加熱容器12に入れ、生
ごみ3を撹拌羽根11で撹拌しながら熱風を生ごみ3に
あて乾燥させ、減量するいわゆる加熱乾燥式生ごみ処理
装置とが一般的に知られている。
2. Description of the Related Art In a conventional garbage treatment apparatus for reducing or reducing the amount of raw garbage, as shown in FIG. 4, microorganisms containing a microbial carrier 1 such as sawdust serving as a habitat of microorganisms Decomposition tank 2, charged garbage 3 and microbial carrier 1
It has a rotary stirring rod 4 and a driving device 5 for mixing and stirring and, and the input garbage 3 is finally decomposed into carbon dioxide and water by microorganisms to reduce the volume of the garbage 3. A heating means 6 for maintaining an appropriate temperature in the microbial decomposition tank 2, a blower 7 for supplying oxygen (air),
A so-called bio-based food waste treatment device that includes control means (not shown) that controls them and decomposes and reduces the amount of food waste by the action of microorganisms, and a heating device 8 and a blower device 9 as shown in FIG. The raw garbage 3 is put in a heating container 12 equipped with a stirring blade 11 which is rotated by a driving device 10 at the bottom, and hot air is applied to the garbage 3 while stirring the raw garbage 3 with the stirring blade 11 to dry the garbage. A so-called heat-drying type food waste processing device is generally known.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、この様
な従来の生ゴミ処理装置では、バイオ式生ごみ処理装置
の場合、微生物が生ごみを分解してゆく方式である為、
この微生物を生息させ、かつ活性化を維持させるための
環境を作る必要がある。そのため、1つには、微生物が
多く生息でき増殖するための場所が必要である。その材
料としては、おがくずのような木片チップ、多孔質のプ
ラスチック片、等の微生物担体が用いられている。
However, in such a conventional food waste disposal device, in the case of the bio-based food waste disposal device, since the microorganisms decompose the food waste,
It is necessary to create an environment for inhabiting this microorganism and maintaining its activation. Therefore, one needs a place where many microorganisms can live and multiply. As the material, a microbial carrier such as a wood chip chip such as sawdust, a porous plastic chip, or the like is used.

【0004】しかし、これらは長時間使用してゆくと、
撹拌による摩擦力で摩耗し、微生物担体が微細化するた
め微生物担体間での空気の通気性が悪くなり、微生物に
よる分解に必要な2つ目の条件である酸素の供給が出来
なくなる。このため、新しい微生物担体への交換が不可
欠となっている。
However, when these are used for a long time,
The microbial carrier is abraded by frictional force due to agitation, and the microbial carrier is miniaturized, so that air permeability between the microbial carriers is deteriorated, and it becomes impossible to supply oxygen, which is the second condition required for microbial decomposition. Therefore, replacement with a new microbial carrier is indispensable.

【0005】また、微生物の生息環境の3つ目として、
適度の湿度が必要であり、乾燥過多の状態では微生物が
生きられず、水分の多い状態でも分解の能力が低下す
る。そして、投入されたこれら微生物担体は処理槽内の
湿度を適度に調整する役目も果たしている。
As the third habitat for microorganisms,
It requires moderate humidity, and microorganisms cannot survive in the excessively dry state, and the ability to decompose is reduced even in the high-moisture state. Then, the introduced microorganism carriers also play a role of appropriately adjusting the humidity in the treatment tank.

【0006】このようにバイオ式生ごみ処理装置では、
微生物で分解するという自然現象を利用した減容方法の
為、減量にかなりの時間がかかると共に、水分の多い材
料が入った場合、このような微生物担体でも水分調整が
きかなくなり、微生物がうまく働かず、分解できずに悪
臭物質が発生することがある。そのためにも、一般的に
は定期的に微生物担体を交換したり、投入物の制限が設
けられ、使い勝手が悪くなるという課題を有していた。
As described above, in the bio-based food waste processing apparatus,
Since this is a volume reduction method that uses a natural phenomenon of being decomposed by microorganisms, it takes a considerable amount of time to reduce the volume, and when a material with a high water content is contained, the water content cannot be adjusted even with such a microbial carrier and the microorganisms work well. In some cases, it cannot be decomposed and a foul-smelling substance is generated. For that reason, in general, there is a problem that the microbial carrier is regularly replaced and the amount of the input material is limited, which deteriorates usability.

【0007】他方、加熱乾燥式生ごみ処理装置の場合
は、ヒータや送風機等の加熱手段を用いて生ごみの水分
を蒸発させ減量化させている為、減量に要する時間はバ
イオ式に比べ大幅に短縮できるが、その分、エネルギを
多く費やされる。すなわち、基本的には生ゴミの水分を
蒸発させるだけなので所定量(生ごみの持つ水分量)以
上の減量ができず、減量に限界があることと、加熱乾燥
式は水分か多ければそれだけエネルギを多く必要とする
と言う課題があった。
On the other hand, in the case of the heat-drying type food waste processing apparatus, the time required for the weight reduction is much larger than that of the bio-type because the water content of the food waste is evaporated by using a heating means such as a heater or a blower. Can be shortened to, but much energy is consumed accordingly. In other words, since basically the water content of food waste is only evaporated, it is not possible to reduce more than a predetermined amount (water content of garbage), and there is a limit to the weight reduction. There was a problem that many were needed.

【0008】本発明は、上記従来の課題を解決するもの
で、減量にあまり多くの時間を必要とせず、微生物担体
を頻繁に交換する等の使い勝手の悪さも無く、水分を蒸
発させるためのエネルギもあまり必要としない、使い勝
手の良い生ゴミ処理装置の提供を目的とする。
The present invention solves the above-mentioned problems of the prior art, does not require too much time for weight reduction, has no inconvenience such as frequent replacement of microbial carriers, and is an energy source for evaporating water. The purpose is to provide an easy-to-use food waste treatment device that does not require much.

【0009】[0009]

【課題を解決するための手段】前記従来の課題を解決す
るたに、本発明の生ゴミ処理装置は、外気の送風により
生ゴミを乾燥する乾燥処理部と、前記乾燥処理部に外気
を供給する第1の送風機と、微生物分解処理部と、前記
乾燥処理部内および前記微生物分解処理部内の生ゴミを
撹拌する撹拌部とを備えた構成としている。
In order to solve the above-mentioned problems of the prior art, a raw garbage processing apparatus of the present invention supplies a drying processing unit for drying raw garbage by blowing the outside air and an outside air to the drying processing unit. The first blower, the microbial decomposition processing unit, and the stirring unit that stirs the garbage in the drying processing unit and the microbial decomposition processing unit.

【0010】これにより、減量にあまり多くの時間を必
要とせず、微生物担体を頻繁に交換する等の使い勝手の
悪さも無く、水分を蒸発させるためのエネルギもあまり
必要としない、使い勝手の良い生ゴミ処理装置を提供で
きる。
As a result, it does not require too much time for weight reduction, has no inconvenience such as frequent replacement of the microorganism carrier, and does not require much energy for evaporating water, and is easy to use. A processing device can be provided.

【0011】[0011]

【発明の実施の形態】請求項1に記載の発明は、外気の
送風により生ゴミを乾燥する乾燥処理部と、前記乾燥処
理部に外気を供給する第1の送風機と、微生物分解処理
部と、前記乾燥処理部内および前記微生物分解処理部内
の生ゴミを撹拌する撹拌部とを備える構成とした。
BEST MODE FOR CARRYING OUT THE INVENTION The invention according to claim 1 is a drying processing section for drying raw garbage by blowing outside air, a first blower for supplying outside air to the drying processing section, and a microbial decomposition processing section. And a stirring unit that stirs the garbage in the drying processing unit and the microbial decomposition processing unit.

【0012】したがって、生ゴミの水分のある程度を送
風による大気熱によって乾燥させることにより省エネル
ギを図り、微生物分解処理部の湿度の上昇を抑制するこ
とにより、分解性能が低下することを防止し、同時に悪
臭の発生も抑制出来るものである。
[0012] Therefore, it is possible to prevent deterioration of the decomposition performance by drying some of the water content of the garbage by the atmospheric heat generated by blowing air to save energy and to suppress the increase in humidity of the microbial decomposition treatment section. At the same time, the generation of foul odor can be suppressed.

【0013】請求項2に記載の発明は、外気の送風によ
り生ゴミを乾燥する乾燥処理部と、前記乾燥処理部に外
気を供給する第1の送風機と、微生物分解処理部と、前
記乾燥処理部内の生ゴミを撹拌する第1の撹拌部と、前
記微生物分解処理部内の生ゴミを撹拌する第2の撹拌部
とを備える構成とした。
According to a second aspect of the present invention, a drying processing section for drying raw garbage by blowing the outside air, a first blower for supplying the outside air to the drying processing section, a microbial decomposition processing section, and the drying processing. The first stirring unit that stirs the raw garbage in the unit and the second stirring unit that stirs the raw garbage in the microbial decomposition processing unit are provided.

【0014】したがって、生ゴミの水分のある程度を送
風による大気熱によって乾燥させることにより省エネル
ギを図り、微生物分解処理部の湿度の上昇を抑制するこ
とにより、分解性能が低下することを防止し、同時に悪
臭の発生も抑制出来るものである。
Therefore, energy can be saved by drying a certain amount of the water content of the garbage by the atmospheric heat generated by the air blow, and the deterioration of the decomposition performance can be prevented by suppressing the increase in the humidity of the microbial decomposition treatment section. At the same time, the generation of foul odor can be suppressed.

【0015】請求項3に記載の発明は、特に、請求項1
または2に記載の乾燥処理部に供給された外気は、微生
物分解処理部を通過する構成とした。
The invention as defined in claim 3 is particularly defined by claim 1.
Alternatively, the outside air supplied to the drying treatment unit described in 2 is configured to pass through the microbial decomposition treatment unit.

【0016】したがって、乾燥処理部内では生ゴミの水
分が蒸発して送風された外気の湿度が上昇する。この高
湿度の空気が微生物分解処理部を通り微生物に必要な酸
素を供給する。この為、水分率の低い乾燥した生ゴミの
投入や冬季等、外気が非常に乾燥している場合でも、微
生物分解処理部の水分の確保が可能であり、微生物分解
処理部での分解性能を維持することが出来るものであ
る。
Therefore, in the drying processing section, the moisture of the raw garbage is evaporated and the humidity of the outside air blown rises. This high-humidity air passes through the microbial decomposition processing section and supplies oxygen necessary for the microorganisms. Therefore, even if the outside air is extremely dry, such as the input of dry raw garbage with a low moisture content, winter, etc., it is possible to secure the water content of the microbial decomposition processing section, and to improve the decomposition performance in the microbial decomposition processing section. It can be maintained.

【0017】請求項4に記載の発明は、特に、請求項1
または2に記載の発明に加えて、脱臭部を備え、乾燥処
理部に供給された外気は、微生物分解処理部を通過後、
前記脱臭部を通過する構成とした。
The invention as defined in claim 4 is particularly characterized by claim 1.
Alternatively, in addition to the invention described in 2, the outside air provided with the deodorizing section and supplied to the drying processing section, after passing through the microbial decomposition processing section,
It was configured to pass through the deodorizing section.

【0018】したがって、生ゴミ処理装置から排気され
る空気の全てを脱臭する為、完全に異臭の発生による不
快感を防止できる。
Therefore, since all the air exhausted from the garbage processing device is deodorized, it is possible to completely prevent the discomfort caused by the generation of the offensive odor.

【0019】請求項5に記載の発明は、特に、請求項1
または2に記載の乾燥処理部に供給された外気を、微生
物分解処理部に通過させる第2の送風機を備える構成と
した。
The invention as defined in claim 5 is particularly defined by claim 1.
Alternatively, the second air blower that allows the outside air supplied to the drying treatment unit described in 2 to pass through the microbial decomposition treatment unit is provided.

【0020】したがって、乾燥処理部内では生ゴミの水
分が蒸発して送風された外気の湿度が上昇する。この高
湿度の空気が、第2の送風機により、微生物分解処理部
を通り微生物に必要な酸素を供給する。この為、水分率
の低い乾燥した生ゴミの投入や冬季等、外気が非常に乾
燥している場合でも、微生物分解処理部の水分の確保が
可能であり、微生物分解処理部での分解性能を維持する
ことが出来るものである。
Therefore, in the drying processing section, the moisture of the raw garbage is evaporated and the humidity of the blown outside air is increased. This high-humidity air passes through the microbial decomposition treatment section and supplies oxygen required for the microorganisms by the second blower. Therefore, even if the outside air is extremely dry, such as the input of dry raw garbage with a low moisture content, winter, etc., it is possible to secure the water content of the microbial decomposition processing section, and to improve the decomposition performance in the microbial decomposition processing section. It can be maintained.

【0021】請求項6に記載の発明は、特に、請求項5
に記載の発明に加えて、脱臭部を備え、微生物分解処理
部を通過した外気を、前記脱臭部に通過させる脱臭送風
機を備える構成とした。
The invention described in claim 6 is particularly characterized by claim 5.
In addition to the invention described in (1) above, a deodorizing blower is provided which has a deodorizing section and allows the outside air that has passed through the microbial decomposition processing section to pass through the deodorizing section.

【0022】したがって、脱臭送風機により、生ゴミ処
理装置から排気される前の空気が全て脱臭部を通過する
ため、生ゴミ処理装置から排気される前の空気を全て脱
臭でき、完全に異臭の発生による不快感を防止できる。
Therefore, since all the air before being discharged from the garbage processing device passes through the deodorizing section by the deodorization blower, all the air before being discharged from the garbage processing device can be deodorized, and a completely offensive odor is generated. It is possible to prevent discomfort caused by.

【0023】請求項7に記載の発明は、特に、請求項1
ないし6のいずれか1項に記載の乾燥処理部に、空気を
循環する循環送風機を備える構成とした。
The invention as defined in claim 7 is particularly defined by claim 1.
The drying treatment unit according to any one of items 1 to 6 is provided with a circulating blower that circulates air.

【0024】そして、循環送風機の送風空気を生ゴミに
当てることにより生ゴミの乾燥を促進でき、処理の短時
間化が図れる。
By applying the air blown by the circulation blower to the garbage, the drying of the garbage can be promoted and the processing time can be shortened.

【0025】また、乾燥処理部に送風する空気の低減が
可能となり脱臭性能の向上、機器のコンパクト化が可能
となる。
Further, it is possible to reduce the air blown to the drying section, improve the deodorizing performance, and make the apparatus compact.

【0026】請求項8に記載の発明は、特に、請求項1
ないし7のいずれか1項に記載の微生物分解処理部を通
過した外気と、乾燥処理部に供給する外気とを熱交換す
る熱交換器部を備える構成とした。
The invention as defined in claim 8 is particularly defined by claim 1.
The heat exchanger part for exchanging heat between the outside air that has passed through the microbial decomposition treatment part according to any one of 1 to 7 and the outside air supplied to the drying treatment part.

【0027】したがって、微生物分解時の発熱で高温と
なり排出する空気で乾燥処理部に供給する空気を加熱で
き、乾燥処理時間を短縮でき、また、外気が低温度の場
合でも生ゴミの乾燥処理を短時間で完了できる。
Therefore, the air supplied to the drying processing section can be heated by the air that is heated to a high temperature due to the heat generated during the microbial decomposition, and the drying processing time can be shortened. Further, even if the outside air is at a low temperature, the garbage can be dried. It can be completed in a short time.

【0028】請求項9に記載の発明は、特に、請求項1
ないし8のいずれか1項に記載の乾燥処理部内の、生ゴ
ミの水分率を検知する水分センサを有し、前記水分セン
サの出力により乾燥処理部から微生物分解処理部に生ゴ
ミを搬送する搬送手段を備える構成とした。
The invention as defined in claim 9 is particularly characterized by claim 1.
9. A transport for transporting raw garbage from the drying treatment unit to the microbial decomposition treatment unit by the output of the moisture sensor, which has a moisture sensor for detecting the moisture content of the raw dust in the drying treatment unit according to any one of 8 to 8 It is configured to include means.

【0029】したがって、微生物分解処理部に投入され
る生ゴミの水分率は一定となり、微生物分解部内の水分
率は微生物の活動に最適に保つことが可能となり、微生
物分解部での分解性能が低下することを防止出来るもの
である。
Therefore, the water content of the garbage introduced into the microbial decomposition section becomes constant, and the water content in the microbial decomposition section can be kept optimal for the activity of microorganisms, and the decomposition performance in the microbial decomposition section deteriorates. It is possible to prevent that.

【0030】[0030]

【実施例】(実施例1)以下、本発明の第1の実施例を
図1の構成図を用いて説明する。図において、13は乾
燥処理部、14は微生物分解処理部、15は脱臭部であ
り、乾燥処理部13と微生物分解処理部14は隣接して
構成している。
(Embodiment 1) A first embodiment of the present invention will be described below with reference to the block diagram of FIG. In the figure, 13 is a drying processing section, 14 is a microbial decomposition processing section, and 15 is a deodorizing section. The drying processing section 13 and the microbial decomposition processing section 14 are adjacent to each other.

【0031】乾燥処理部13は、生ゴミ投入口16と、
生ゴミ排出口17と、第1の送風機18と、外気入口1
9と、外気入口19近傍に設けた加熱装置として補助ヒ
ータ20と、撹拌部21、及びこれらの運転制御手段
(図示せず)等より構成している。撹拌部21は、撹拌
モータ22と、乾燥処理部13内に設けた羽根23と微
生物分解処理部14内に設けた羽根24を撹拌軸25で
連結し一体として回転する構成を示したが、例えば、第
1、第2の撹拌部というように撹拌部を別々に設ける、
あるいは撹拌軸25を個別に構成してベルト、歯車等で
連結しても良い。
The drying processing section 13 includes a garbage input port 16 and
Garbage discharge outlet 17, first blower 18, outside air inlet 1
9, an auxiliary heater 20 as a heating device provided in the vicinity of the outside air inlet 19, an agitator 21, and operation control means (not shown) for these, and the like. The stirring unit 21 has a configuration in which the stirring motor 22, the blades 23 provided in the drying processing unit 13 and the blades 24 provided in the microbial decomposition processing unit 14 are connected by a stirring shaft 25 and integrally rotated. , The first and second stirring units are separately provided,
Alternatively, the stirring shaft 25 may be individually configured and connected by a belt, a gear, or the like.

【0032】微生物分解処理部14は、生ゴミ排出口1
7に開口し、排出口に第2の送風機26と、脱臭部15
に開口した排気口27と、内部に撹拌部21の羽根2
4、及びこれらの運転制御手段(図示せず)等より構成
している。
The microbial decomposition processing section 14 is provided with the garbage discharge port 1.
7, the second blower 26 at the outlet and the deodorizing unit 15
The exhaust port 27 opened to the inside and the blade 2 of the stirring section 21 inside
4 and their operation control means (not shown) and the like.

【0033】脱臭部15は、排気口27から加熱ヒータ
28、脱臭触媒29、脱臭送風機30を通り外部に通路
を構成してある。
The deodorizing section 15 has a passage outside from the exhaust port 27 through the heater 28, the deodorizing catalyst 29, and the deodorizing blower 30.

【0034】また、微生物分解処理部14には、生ゴミ
を微生物で分解処理した後の残差物の排出する残差出口
31を設け、この残差出口28は残差物を一時保持する
肥料溜32に結合してある。
Further, the microbial decomposition processing section 14 is provided with a residual outlet 31 for discharging the residual substances after the raw garbage is decomposed by microorganisms, and the residual outlet 28 is a fertilizer for temporarily holding the residual substances. It is connected to the reservoir 32.

【0035】また、正常時は微生物分解処理部14内
は、微生物の分解熱により高温となり温度調節を必要と
しないが微生物分解の初期等の補助として加熱するヒー
タ(図示せず)と温度制御手段を設けても良い。
Further, in a normal state, the temperature inside the microbial decomposition processing section 14 becomes high due to the decomposition heat of the microorganisms and the temperature control is not required, but a heater (not shown) and a temperature control means for heating to assist the initial stage of microbial decomposition etc. May be provided.

【0036】そして、このような構成において、まず、
生ゴミ3を乾燥処理部13の生ゴミ投入口16から投入
され、撹拌部21の羽根23で撹拌されながら、外気入
口19からの空気で水分の蒸発を促進する。外気の湿度
が非常に高い場合等は補助ヒータ20を通電する。生ゴ
ミの水分が50%程度まで蒸発した後、生ゴミは羽根2
3の回転により掻き上げられて、生ゴミ排出口17から
微生物分解処理部14に移動する。微生物分解処理部1
4の中で生ゴミは、羽根24の撹拌により微生物担体1
と混合し微生物により分解され、二酸化炭素と水になっ
てゆく。そして、生ゴミの分解しきれない残差物は、残
差出口31から肥料溜32に移動して残差物を一時保持
し、適時取り出し肥料として利用する。
Then, in such a configuration, first,
The garbage 3 is introduced from the garbage introduction port 16 of the drying processing unit 13 and is stirred by the blades 23 of the stirring unit 21, while the air from the outside air inlet 19 promotes evaporation of water. When the humidity of the outside air is very high, the auxiliary heater 20 is energized. After the water content of the garbage has evaporated to about 50%,
It is scraped up by the rotation of 3, and moved from the garbage discharge port 17 to the microbial decomposition processing section 14. Microbial decomposition processing section 1
The garbage in 4 is the microorganism carrier 1 by stirring the blades 24.
It is mixed with and decomposed by microorganisms to become carbon dioxide and water. Then, the residual substance that cannot be completely decomposed into raw garbage moves from the residual outlet 31 to the fertilizer reservoir 32 to temporarily hold the residual substance and take it out as appropriate and use it as fertilizer.

【0037】また、投入した生ゴミ3や微生物分解処理
部14で臭いが強い時は、脱臭送風機30を運転する。
乾燥処理部13或いは微生物分解処理部14の臭いのあ
る空気は、生ゴミ排出口17、排気口27を通り加熱ヒ
ータ28で加温され高温となって脱臭触媒29で臭い成
分が分解され、脱臭送風機30から外部に放出する。
When the introduced garbage 3 or the microbial decomposition processing section 14 has a strong odor, the deodorizing blower 30 is operated.
The odorous air of the drying processing section 13 or the microbial decomposition processing section 14 is heated by the heater 28 through the garbage discharge port 17 and the exhaust port 27 to reach a high temperature, and the odorous components are decomposed by the deodorization catalyst 29 to deodorize. The air is discharged from the blower 30 to the outside.

【0038】このように、乾燥処理部13と微生物分解
処理部14を隣接させて構成し、生ゴミの水分のある程
度を送風による大気熱によって乾燥させることにより省
エネルギを図れる。
As described above, the drying processing section 13 and the microbial decomposition processing section 14 are arranged adjacent to each other, and a certain amount of water in the garbage is dried by the atmospheric heat generated by the blown air to save energy.

【0039】すなわち、生ゴミの水分蒸発熱を従来は電
気ヒータの熱を利用していたが、生ゴミに空気を流し空
気からこの蒸発熱を取り気化させる。このため、生ゴミ
や空気は温度が低下し蒸発量が低下する。他方、微生物
分解処理部14では、生ゴミを微生物が分解する時熱が
発生し高温となる。そこで、乾燥処理部13と微生物分
解処理部14を密接させた事により、微生物の分解熱で
乾燥処理部13を加熱し生ゴミの水分蒸発に利用でき
る。この様に、生ゴミの乾燥処理時のエネルギは大半が
大気熱と微生物分解熱であり、送風の為の送風機の電気
のみであり、使用電力量は大幅に低減できる。
That is, the heat of the electric heater has conventionally been used for the heat of evaporation of water from the garbage, but air is passed through the garbage and the heat of evaporation is taken from the air to be vaporized. For this reason, the temperature of raw garbage and air decreases, and the amount of evaporation decreases. On the other hand, in the microbial decomposition processing unit 14, heat is generated and the temperature becomes high when microorganisms decompose the garbage. Therefore, by bringing the drying treatment section 13 and the microorganism decomposition treatment section 14 into close contact with each other, the drying treatment section 13 can be heated by the heat of decomposition of the microorganisms and used to evaporate the water content of garbage. As described above, most of the energy during the drying process of the garbage is the atmospheric heat and the heat of microbial decomposition, and only the electricity of the blower for blowing air is used, and the power consumption can be greatly reduced.

【0040】また、微生物分解部14の湿度の上昇を抑
制することができ、分解性能が低下することを防止し、
同時に悪臭の発生も抑制出来るものである。
Further, it is possible to suppress an increase in the humidity of the microbial decomposition portion 14 and prevent deterioration of the decomposition performance,
At the same time, the generation of foul odor can be suppressed.

【0041】すなわち、生ゴミの水分率は標準的には8
0%程度で安定しているが、液体の汁物等と混在したま
まの場合は水分が著しく多い時がある。水分の多い材料
が入った場合、微生物がうまく働かず、分解できずに悪
臭物質が発生するる。そのためにも、一般的には定期的
に微生物担体を交換したり、投入物の制限が設けられて
たが、実施例では、乾燥処理部13で予め水分をある程
度蒸発により除去して後、微生物分解処理部14に導入
することにより、微生物分解処理部14に入る生ゴミが
最初どのような状態であれ常に一定の水分率を維持した
状態で入ってくるため、微生物にとってよい環境を実現
でき、微生物による分解処理が常に安定した状態で行う
ことが出来る。これにより、悪臭等の発生もなくなる。
That is, the water content of raw garbage is typically 8
It is stable at about 0%, but when it remains mixed with liquid soup, the water content may be remarkably high. When a high-moisture material is contained, microorganisms do not work well and cannot be decomposed, and a malodorous substance is generated. For that reason, generally, the microbial carrier is regularly replaced or the input is limited. However, in the embodiment, after the moisture is removed to some extent in advance by the drying treatment unit 13, the microorganisms are removed. By introducing it into the decomposition processing unit 14, the garbage entering the microbial decomposition processing unit 14 always enters with a constant water content regardless of the state, so that a good environment for microorganisms can be realized. The decomposition treatment by microorganisms can always be performed in a stable state. This eliminates the generation of foul odors.

【0042】(実施例2)次に、本発明の第2の実施例
を図2の構成図を用いて説明する。図2は、本発明の実
施例2における生ごみ処理装置の全体構成を示す。
(Embodiment 2) Next, a second embodiment of the present invention will be described with reference to the configuration diagram of FIG. FIG. 2 shows the overall configuration of a food waste processing device according to a second embodiment of the present invention.

【0043】実施例1と異なるところは、乾燥処理部1
3内に空気を循環する循環送風機33を設けてあり、こ
の循環送風機33によって乾燥処理部13内の空気を循
環する。循環送風機33の送風空気を生ゴミに当てるこ
とにより生ゴミの乾燥を促進でき、処理の短時間化が図
れる。すなわち、外気入口19から入った空気により生
ゴミの水分が蒸発するが、この蒸発した水分が生ゴミの
周辺に滞在した分は空気の水蒸気圧が上昇し蒸発速度が
遅くなった。そこで、循環送風機33の送風空気を生ゴ
ミに当てることにより、この水蒸気を掃気して生ゴミの
周囲空気の水蒸気圧を下げ水分の蒸発を早める事ができ
る。
The difference from the first embodiment is that the drying processing unit 1
A circulating fan 33 for circulating air is provided in the air conditioning unit 3, and the air in the drying processing unit 13 is circulated by the circulating fan 33. By applying the air blown by the circulation fan 33 to the garbage, the drying of the garbage can be promoted and the processing time can be shortened. That is, the moisture of raw garbage is evaporated by the air entering from the outside air inlet 19, but the vapor pressure of the air is increased and the evaporation rate is slowed down by the amount of the evaporated moisture staying around the raw garbage. Therefore, the air blown by the circulation blower 33 is applied to the garbage to scavenge the water vapor to lower the water vapor pressure of the air surrounding the garbage and accelerate the evaporation of water.

【0044】また、乾燥処理部13に送風する空気の低
減が可能となり脱臭性能の向上、機器のコンパクト化が
可能となる。
Further, the air blown to the drying processing section 13 can be reduced, the deodorizing performance can be improved, and the equipment can be made compact.

【0045】また、外気を第2の送風機26により乾燥
処理部13に導入後、微生物分解処理部14を通り排出
する構成により、乾燥処理部13内では生ゴミの水分が
蒸発して送風された外気の湿度が上昇する。この高湿度
の空気が微生物分解処理部14を通り微生物に必要な酸
素を供給した後、外部に排出する。この為、水分率の低
い乾燥した生ゴミの投入や、冬季等、外気が非常に乾燥
している場合でも、微生物分解処理部14の水分の確保
が可能であり、微生物分解処理部14での分解性能を維
持することが出来るものである。
In addition, after the outside air is introduced into the drying treatment section 13 by the second blower 26 and discharged through the microbial decomposition treatment section 14, the moisture of the raw garbage is evaporated and blown in the drying treatment section 13. The humidity of the outside air rises. This high-humidity air passes through the microbial decomposition processing section 14 and supplies oxygen necessary for the microorganisms, and then discharges it to the outside. Therefore, it is possible to ensure the water content of the microbial decomposition processing unit 14 even when the dry garbage having a low water content is input or the outside air is extremely dry such as in the winter season. The decomposition performance can be maintained.

【0046】また、外気を脱臭送風機30の吸引により
乾燥処理部13に導入後、微生物分解処理部14を通
り、さらに脱臭部15に導き、その後排出する構成に設
けたことにより、生ゴミ処理機から出ていく空気の全て
を脱臭する為、完全に異臭の発生による不快感を防止で
きる。
In addition, after the outside air is introduced into the drying processing section 13 by suction of the deodorizing blower 30, it passes through the microbial decomposition processing section 14, is further guided to the deodorizing section 15, and is then discharged. Since all the air that comes out of the room is deodorized, it is possible to completely prevent the discomfort caused by the generation of an offensive odor.

【0047】また、外気を乾燥処理部13に導入後排出
する第1の送風機18、または外気を乾燥処理部13に
導入後、微生物分解処理部14を通り排出する第2送風
機26と、外気を乾燥処理部14に導入後、微生物分解
処理部14を通り、さらに脱臭部15に導き、その後排
出する脱臭送風機30を設けてある。このことにより生
ゴミの臭いの発生レベルに応じて外気の流れる流路を切
り替える事が可能となり、外部に臭いの発生を抑制し且
つ短時間処理と省エネ化が可能となる。すなわち、乾燥
処理部13に投入する生ゴミが野菜果物等の臭いが比較
的少ない場合は、第1の送風機18または第2の送風機
26により大風量の空気を直接排出して短時間に乾燥処
理を完了する。
Further, the first blower 18 for introducing the outside air into the drying processing section 13 and then discharging it, or the second blower 26 for introducing the outside air into the drying processing section 13 and discharging it through the microbial decomposition processing section 14, and the outside air. A deodorizing blower 30 is provided, which is introduced into the drying processing section 14, passes through the microbial decomposition processing section 14, further leads to the deodorizing section 15, and is then discharged. As a result, it is possible to switch the flow path of the outside air according to the level of the smell of raw garbage, which suppresses the generation of the smell to the outside, and enables short-time processing and energy saving. That is, when the odor of vegetables, fruits, etc. input to the drying processing unit 13 is relatively small, a large amount of air is directly discharged by the first blower 18 or the second blower 26 to perform the drying treatment in a short time. To complete.

【0048】また、生ゴミが腐っている物等臭いが強い
場合は、脱臭送風機30により生ゴミ処理機から出てい
く空気の全てを脱臭する為、完全に異臭の発生による不
快感を防止できる。
When the garbage has a strong odor, such as rotten food, the deodorant blower 30 deodorizes all the air discharged from the garbage processor, so that the unpleasant odor caused by the offensive odor can be completely prevented. .

【0049】(実施例3)次に、本発明の第3の実施例
を図3の構成図を用いて説明する。図3は、本発明の実
施例3における生ごみ処理装置の全体構成を示す。
(Third Embodiment) Next, a third embodiment of the present invention will be described with reference to the block diagram of FIG. FIG. 3 shows the overall configuration of a food waste processing device according to a third embodiment of the present invention.

【0050】実施例1と異なるところは、微生物分解処
理部14から排出する空気出口である第2の送風機26
と、乾燥処理部13に供給する空気入口である外気入口
19との間を熱交換する熱交換器部34を構成してあ
る。
The difference from the first embodiment is that the second blower 26, which is an air outlet for discharging from the microbial decomposition processing section 14, is used.
And the outside air inlet 19 which is an air inlet for supplying to the drying processing unit 13 are configured to form a heat exchanger unit 34.

【0051】すなわち、微生物分解処理部14から排出
する空気と乾燥処理部13に供給する空気とを熱交換す
る熱交換器部34を構成したことにより、微生物分解処
理部14内で微生物分解時の発熱で高温となり排出する
空気を用いて乾燥処理部13に供給する空気を加熱で
き、乾燥処理時間を短縮でき、また、外気が低温度の場
合でも生ゴミの乾燥処理を短時間で完了できる。
That is, by constructing the heat exchanger section 34 for exchanging heat between the air discharged from the microbial decomposition processing section 14 and the air supplied to the drying processing section 13, the microbial decomposition processing section 14 at the time of microbial decomposition is constituted. It is possible to heat the air supplied to the drying processing unit 13 by using the air that becomes high temperature due to heat generation and is discharged, so that the drying processing time can be shortened, and the drying processing of the garbage can be completed in a short time even when the outside air has a low temperature.

【0052】また、乾燥処理部13内の生ゴミの水分率
を検知する水分センサ18を設け、この水分センサ18
の出力により乾燥処理部13から微生物分解処理部14
に生ゴミを搬送する搬送手段を有する構成により、微生
物分解処理部14に投入される生ゴミの水分率は一定と
なり微生物分解部14内の水分率は微生物の活動に最適
に保つことが可能となり、微生物分解部での分解性能が
低下することを防止出来るものであり、微生物による分
解処理が常に安定した状態で行うことが出来、悪臭等の
発生もなくなるものである。
Further, a moisture sensor 18 for detecting the moisture content of the garbage in the drying processing section 13 is provided.
Output from the drying processing unit 13 to the microbial decomposition processing unit 14
Due to the configuration having the transporting means for transporting the raw garbage, the water content of the raw garbage introduced into the microbial decomposition processing section 14 becomes constant, and the water content in the microbial decomposition section 14 can be kept optimal for the activity of the microorganism. In addition, it is possible to prevent deterioration of the decomposition performance in the microbial decomposition part, and it is possible to carry out the decomposition treatment by microorganisms in a stable state at all times and to eliminate the generation of foul odors.

【0053】[0053]

【発明の効果】以上のように、請求項1〜9に記載の発
明によれば、生ゴミの水分のある程度を送風による大気
熱によって乾燥させることにより省エネルギを図り、微
生物分解処理部の湿度の上昇を抑制することにより、分
解性能が低下することを防止し、同時に悪臭の発生も抑
制出来る生ゴミ処理装置を提供できる。
As described above, according to the invention described in claims 1 to 9, energy can be saved by drying a certain amount of water content of raw garbage by atmospheric heat by blowing air, and humidity of the microbial decomposition treatment section can be improved. It is possible to provide a garbage processing device that can prevent degradation of decomposition performance and suppress generation of foul odor at the same time by suppressing the increase in the amount of odor.

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

【図1】本発明の第1の実施例における生ゴミ処理機の
構成図
FIG. 1 is a configuration diagram of a garbage disposal according to a first embodiment of the present invention.

【図2】本発明の第2の実施例における生ゴミ処理機の
構成図
FIG. 2 is a configuration diagram of a garbage disposal according to a second embodiment of the present invention.

【図3】本発明の第3の実施例における生ゴミ処理機の
構成図
FIG. 3 is a block diagram of a garbage disposal according to a third embodiment of the present invention.

【図4】従来の生ゴミ処理機の縦断面図FIG. 4 is a vertical sectional view of a conventional garbage processing machine.

【図5】従来の他の生ゴミ処理機の縦断面図FIG. 5 is a vertical sectional view of another conventional food waste processing machine.

【符号の説明】[Explanation of symbols]

13 乾燥処理部 14 微生物分解部 15 脱臭部 18 第1の送風機 21 撹拌部 26 第2の送風機 30 脱臭送風機 33 循環送風機 34 熱交換器部 35 水分センサ 13 Drying processing section 14 Microbial decomposition section 15 Deodorizing part 18 First Blower 21 Stirrer 26 Second blower 30 deodorant blower 33 Circulation blower 34 Heat Exchanger Section 35 Moisture sensor

フロントページの続き (72)発明者 羽田野 剛 大阪府門真市大字門真1006番地 松下電器 産業株式会社内 (72)発明者 河合 雅信 大阪府門真市大字門真1006番地 松下電器 産業株式会社内 (72)発明者 西田 博史 大阪府門真市大字門真1006番地 松下電器 産業株式会社内 Fターム(参考) 3L113 AA07 AB06 AC08 AC58 AC87 CA02 DA02 DA10 4D004 AA03 CA15 CA19 CA22 CA42 CA48 CB04 CB28 CB31 CB32 CB44 CB45 CC08 CC09 DA01 DA02 DA09 4D048 AA22 CC32 CC38 Continued front page    (72) Inventor Tsuyoshi Hatano             1006 Kadoma, Kadoma-shi, Osaka Matsushita Electric             Sangyo Co., Ltd. (72) Inventor Masanobu Kawai             1006 Kadoma, Kadoma-shi, Osaka Matsushita Electric             Sangyo Co., Ltd. (72) Inventor Hiroshi Nishida             1006 Kadoma, Kadoma-shi, Osaka Matsushita Electric             Sangyo Co., Ltd. F term (reference) 3L113 AA07 AB06 AC08 AC58 AC87                       CA02 DA02 DA10                 4D004 AA03 CA15 CA19 CA22 CA42                       CA48 CB04 CB28 CB31 CB32                       CB44 CB45 CC08 CC09 DA01                       DA02 DA09                 4D048 AA22 CC32 CC38

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 外気の送風により生ゴミを乾燥する乾燥
処理部と、前記乾燥処理部に外気を供給する第1の送風
機と、微生物分解処理部と、前記乾燥処理部内および前
記微生物分解処理部内の生ゴミを撹拌する撹拌部とを備
えた生ゴミ処理装置。
1. A drying processing unit for drying raw garbage by blowing outside air, a first blower for supplying outside air to the drying processing unit, a microbial decomposition processing unit, and inside the drying processing unit and inside the microbial decomposition processing unit. An apparatus for treating food waste, which is provided with a stirrer for stirring the food waste.
【請求項2】 外気の送風により生ゴミを乾燥する乾燥
処理部と、前記乾燥処理部に外気を供給する第1の送風
機と、微生物分解処理部と、前記乾燥処理部内の生ゴミ
を撹拌する第1の撹拌部と、前記微生物分解処理部内の
生ゴミを撹拌する第2の撹拌部とを備えた生ゴミ処理装
置。
2. A drying processing unit for drying raw garbage by blowing the outside air, a first blower for supplying the outside air to the drying processing unit, a microbial decomposition treatment unit, and stirring the raw garbage in the drying processing unit. A raw garbage processing device comprising a first agitating section and a second agitating section for agitating the raw garbage in the microbial decomposition processing section.
【請求項3】 乾燥処理部に供給された外気は、微生物
分解処理部を通過する構成とした請求項1または2に記
載の生ゴミ処理装置。
3. The garbage treatment device according to claim 1, wherein the outside air supplied to the drying processing section is configured to pass through the microbial decomposition processing section.
【請求項4】 脱臭部を備え、乾燥処理部に供給された
外気は、微生物分解処理部を通過後、前記脱臭部を通過
する構成とした請求項1または2に記載の生ゴミ処理装
置。
4. The garbage processing device according to claim 1, further comprising a deodorizing unit, wherein the outside air supplied to the drying processing unit passes through the microbial decomposition processing unit and then passes through the deodorizing unit.
【請求項5】 乾燥処理部に供給された外気を、微生物
分解処理部に通過させる第2の送風機を備えた請求項1
または2に記載の生ゴミ処理装置。
5. A second blower for allowing the outside air supplied to the drying processing section to pass through the microbial decomposition processing section.
Alternatively, the garbage disposal according to item 2.
【請求項6】 脱臭部を備え、微生物分解処理部を通過
した外気を、前記脱臭部に通過させる脱臭送風機を備え
た請求項5に記載の生ゴミ処理装置。
6. The garbage processing device according to claim 5, further comprising a deodorizing blower that has a deodorizing section and that allows the outside air that has passed through the microbial decomposition processing section to pass through the deodorizing section.
【請求項7】 乾燥処理部に、空気を循環する循環送風
機を備えた請求項1ないし6のいずれか1項に記載の生
ゴミ処理装置。
7. The garbage treatment device according to claim 1, wherein the drying treatment section is provided with a circulation blower for circulating air.
【請求項8】 微生物分解処理部を通過した外気と、乾
燥処理部に供給する外気とを熱交換する熱交換器部を備
えた請求項1ないし7のいずれか1項に記載の生ゴミ処
理装置。
8. The raw garbage treatment according to claim 1, further comprising a heat exchanger section for exchanging heat between the outside air that has passed through the microbial decomposition processing section and the outside air that is supplied to the drying processing section. apparatus.
【請求項9】 乾燥処理部内の生ゴミの水分率を検知す
る水分センサを有し、前記水分センサの出力により乾燥
処理部から微生物分解処理部に生ゴミを搬送する搬送手
段を備えた請求項1ないし8のいずれか1項に記載の生
ゴミ処理装置。
9. A moisture sensor for detecting the moisture content of raw garbage in the drying processing section, and a transporting means for transporting the raw garbage from the drying processing section to the microbial decomposition processing section according to the output of the moisture sensor. 9. The garbage treatment device according to any one of 1 to 8.
JP2002049094A 2002-02-26 2002-02-26 Garbage disposal equipment Expired - Fee Related JP3843862B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2002049094A JP3843862B2 (en) 2002-02-26 2002-02-26 Garbage disposal equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2002049094A JP3843862B2 (en) 2002-02-26 2002-02-26 Garbage disposal equipment

Publications (2)

Publication Number Publication Date
JP2003245640A true JP2003245640A (en) 2003-09-02
JP3843862B2 JP3843862B2 (en) 2006-11-08

Family

ID=28661694

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Link
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006263636A (en) * 2005-03-25 2006-10-05 Peace Sangyo Kk Garbage disposal apparatus
CN108106364A (en) * 2017-12-11 2018-06-01 周兰芝 Medicinal planet gear type drying equipment in one kind
CN114671188A (en) * 2022-03-10 2022-06-28 北京中科博联科技集团有限公司 Odor leakage prevention type belt conveyor bin door butt joint structure of aerobic fermentation bin

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006263636A (en) * 2005-03-25 2006-10-05 Peace Sangyo Kk Garbage disposal apparatus
CN108106364A (en) * 2017-12-11 2018-06-01 周兰芝 Medicinal planet gear type drying equipment in one kind
CN114671188A (en) * 2022-03-10 2022-06-28 北京中科博联科技集团有限公司 Odor leakage prevention type belt conveyor bin door butt joint structure of aerobic fermentation bin
CN114671188B (en) * 2022-03-10 2023-11-17 北京中科博联科技集团有限公司 Butt joint structure of bin gate of anti-odor leakage type belt conveyor of aerobic fermentation bin

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