JP2002018406A - Biodegradation promoting block, biodegradation apparatus, and organic waste decomposition method using the same - Google Patents

Biodegradation promoting block, biodegradation apparatus, and organic waste decomposition method using the same

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Publication number
JP2002018406A
JP2002018406A JP2000206440A JP2000206440A JP2002018406A JP 2002018406 A JP2002018406 A JP 2002018406A JP 2000206440 A JP2000206440 A JP 2000206440A JP 2000206440 A JP2000206440 A JP 2000206440A JP 2002018406 A JP2002018406 A JP 2002018406A
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JP
Japan
Prior art keywords
biodegradation
organic waste
organic
closed container
microorganisms
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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
JP2000206440A
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Japanese (ja)
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JP3946939B2 (en
Inventor
浩次 ▲高▼▲巣▼
Koji Takasu
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Individual
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Individual
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Publication of JP2002018406A publication Critical patent/JP2002018406A/en
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Abstract

PROBLEM TO BE SOLVED: To provide an apparatus and a treatment manner capable of further efficiently carrying out biodegradation of organic wastes by microorganism in consideration of problems relevant to the biodegradation. SOLUTION: A closed container 1 of a biodegradation apparatus is charged with biodegradation promoting blocks 2 and organic wastes 3, the organic wastes 3 are heated indirectly and directly by heating the closed container 1 as a whole and blowing a hot air F and while the temperature of the organic wastes 3 being kept in a temperature range suitable for propagation of the microorganism, the organic wastes 3 are physically pulverized by the outer face of the biodegradation promoting blocks 2 and simultaneously the microorganism adhering to the biodegradation promoting blocks 2 is evenly dispersed, so that the biodegradation of the organic wastes 3 by microorganism is promoted.

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、有機物の生分解を
促進する生分解促進ブロック及び生分解処理装置と、こ
れらを用いてホテル、旅館、飲食店や家庭から排出され
る生ごみ、有機産業廃棄物、海産物残渣、下水汚泥、糞
尿汚泥やその他有機性廃棄物(以下、有機廃棄物で総称
する)を生分解する有機廃棄物分解処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a biodegradation accelerating block and a biodegradation treatment device for accelerating the biodegradation of organic matter, and the garbage discharged from hotels, inns, restaurants and homes using these, and the organic industry. The present invention relates to an organic waste decomposition treatment method for biodegrading wastes, marine residues, sewage sludge, manure sludge, and other organic wastes (hereinafter collectively referred to as organic wastes).

【0002】[0002]

【従来の技術】有機廃棄物は、直接的には自然を害しな
いものが多いため、廃棄処分も焼却、埋立又は海洋投棄
等、様々な態様が利用できる。しかし、焼却処分ではダ
イオキシンの発生が問題視されたり、埋立処分では埋立
地確保が現実的に難しく、海洋投棄では海の汚染防止の
観点から、条約により前面禁止されるに至っている。そ
こで、注目され始めた処分態様が、微生物の働きを利用
した生分解処分である。
2. Description of the Related Art Since many organic wastes do not directly harm nature, various modes of disposal such as incineration, landfill or ocean dumping can be used. However, the generation of dioxin is regarded as a problem in incineration, and it is practically difficult to secure landfill sites in landfills. In the case of ocean dumping, the convention has been banned from the viewpoint of preventing pollution of the sea. Therefore, a disposal mode that has begun to attract attention is biodegradation disposal utilizing the action of microorganisms.

【0003】上記生分解処分では、密閉容器内へ投入し
た有機廃棄物を一定温度に保つことで、有機廃棄物に付
着したり、大気中にいた微生物を、有機廃棄物内で繁殖
させたり、有機廃棄物の生分解を促し、有機廃棄物を水
と二酸化炭素に分解する。前記微生物の生分解による処
分をよりよく実施するには、(1)微生物が最も活動しや
すい温度の維持、(2)微生物が生分解しやすい大きさま
での有機廃棄物の物理的破砕、そして(3)有機廃棄物に
対する微生物の均一な分散が重要となる。
[0003] In the biodegradation disposal, by keeping the organic waste put in a closed container at a constant temperature, microorganisms attached to the organic waste or microorganisms in the atmosphere can be propagated in the organic waste. Promotes biodegradation of organic waste and decomposes organic waste into water and carbon dioxide. To better implement the biodegradation of said microorganisms, (1) maintaining the temperature at which the microorganisms are most active, (2) physically breaking down organic waste to a size at which the microorganisms are more likely to biodegrade, and ( 3) Uniform dispersion of microorganisms in organic waste is important.

【0004】上記の点について、基本的には密閉容器の
加温と密閉容器内に設けた攪拌羽根とによって解決して
きたが、近年では、更に補助的に有機廃棄物と共に密閉
容器に投入する補助部材が用いられるようになってきて
いる。例えば、特開平08-109086号では、微生物を付着
させた多孔質の木片等を有機廃棄物と共に密閉容器に投
入、攪拌、混合する技術を、また特開平11-347526号で
は、内部に有機廃棄物の出入りを可能にする中空構造と
した充填材を有機廃棄物と共に密閉容器内へ投入し、攪
拌、混合する技術を、それぞれ開示している。
[0004] The above-mentioned points have been basically solved by heating the closed container and stirring blades provided in the closed container. Members are being used. For example, Japanese Patent Application Laid-Open No. 08-109086 discloses a technique in which a porous wood piece or the like to which microorganisms are attached is put into a closed container together with organic waste, agitated, and mixed, and Japanese Patent Application Laid-Open No. 11-347526 discloses an organic waste internally. Disclosed is a technique in which a filler having a hollow structure that allows entry and exit of an object is charged into an airtight container together with organic waste, followed by stirring and mixing, respectively.

【0005】[0005]

【発明が解決しようとする課題】特開平08-109086号と
特開平11-347526号とは、有機廃棄物と共に多孔質の木
片を密閉容器内へ投入するか、耐摩耗性を備えたプラス
チック又は金属製中空構造成形品を投入するかに相違点
がある。前者は、木片が有する微少な孔に、後者は中空
構造を具現化するパイプ内に、それぞれ微生物を潜ませ
る。働きとして両者は等価であるが、木片は分解途中の
廃液を吸収して保持してしまうために異臭を放ちやす
く、強度の点からもプラスチック又は金属製中空構造成
形品には劣る違いがある。しかし、金属製中空構造成形
品は強度があり過ぎて、密閉容器を傷つける虞れがある
ので好ましくない。
SUMMARY OF THE INVENTION Japanese Patent Application Laid-Open Nos. 08-109086 and 11-347526 disclose a method in which a porous wooden piece is put into an airtight container together with organic waste, or a plastic or abrasion-resistant plastic is used. There is a difference in whether a metal hollow structure molded product is introduced. In the former, microorganisms are buried in microscopic holes of a piece of wood, and in the latter, microorganisms are buried in a pipe embodying a hollow structure. Although the two are equivalent in function, the wood chips absorb and retain the waste liquid in the course of decomposition, so that they easily emit an unpleasant odor, and are inferior to plastic or metal hollow structure molded articles in terms of strength. However, a metal hollow structure molded article is not preferable because it has too strong strength and may damage the closed container.

【0006】生分解処分で重要なのは、密閉容器内の環
境を整えること、すなわち上記(1),(2)及び(3)の条件を
よりよく満たすことにある。例えば、(1)微生物が最も
活動しやすい温度の維持については、単純に密閉容器を
暖めるだけでは、密閉容器内へ投入する有機廃棄物の量
が増えるほど部分的に温度差が生じてしまう。こうした
温度分布のばらつきは、微生物の働きを妨げる要因にな
りかねない。特開平11-347526号では、攪拌羽根に設け
た多数の通気孔を設け、この通気孔から満遍なく温風を
吹き出すようにしているが、この通気孔については、次
の(2)の条件(有機廃棄物の破砕)との絡みで、有機廃棄
物を微細化するほど通気孔が塞がれる可能性が増大する
という問題が発生する。
What is important in biodegradation disposal is to prepare the environment in a closed container, that is, to better satisfy the conditions (1), (2) and (3). For example, (1) With respect to maintaining a temperature at which microorganisms are most likely to be active, simply heating a closed container may cause a partial temperature difference as the amount of organic waste put into the closed container increases. Such variation in the temperature distribution may be a factor that hinders the action of microorganisms. In Japanese Patent Application Laid-Open No. H11-347526, a large number of ventilation holes are provided in a stirring blade so that warm air is blown out uniformly from the ventilation holes. (Crushing of waste), there is a problem that as the size of the organic waste is reduced, the possibility of blocking the vent increases.

【0007】微生物による生分解はミクロ的な働きであ
り、有機廃棄物をよりよく分解するには、まず物理的に
有機廃棄物をできる限り細かく破砕しておく方が好まし
い(上記(2)の条件)。このため、従来は、多数の羽根や
突起を備えた攪拌羽根を回転させて有機廃棄物を破砕す
るようにしている。更に、特開平08-109086号や特開平1
1-347526号では、有機廃棄物と共に密閉容器に投入した
木片やプラスチック又は金属製中空構造成形品の衝突又
は摺り合わせ等によって、有機廃棄物の破砕を試みてい
るが、木片では破砕力が低く、また円筒状のプラスチッ
ク又は金属製中空構造成形品では、摩擦力は期待できる
が、破砕力はそれほど期待できない。
[0007] Biodegradation by microorganisms is a microscopic function, and in order to decompose organic waste better, it is preferable to first physically break the organic waste as finely as possible (see (2) above). conditions). For this reason, conventionally, an agitation blade provided with a large number of blades and projections is rotated to crush organic waste. Further, Japanese Patent Application Laid-Open No. 08-109086 and
In 1-347526, crushing of organic waste is attempted by collision or rubbing of wood chips or plastic or metal hollow structure molded products put into a closed container together with organic waste, but the crushing power of wood chips is low. In the case of a cylindrical plastic or metal hollow structure molded product, a frictional force can be expected, but a crushing force cannot be expected so much.

【0008】(3)有機廃棄物に対する微生物の均一な分
散については、特開平08-109086号及び特開平11-347526
号のいずれも、木片やプラスチック又は金属製中空構造
成形品に付着して微生物が分散するため、期待できる。
しかし、木片では水分を吸収して微生物が潜むべき微細
孔を防いでしまう。また、プラスチック又は金属製中空
構造成形品では、中空構造部位が大きすぎると破砕した
有機物の出入りが多くなって微生物が排出されてしまう
し、小さすぎると有機物が目詰まりを起こす等、中空構
造だけでは微生物の分散が確実ではないと推察される。
こうした問題点を鑑み、より効率的に微生物による生分
解が可能となるように、分解処理全般の見直しを進め、
検討した。
(3) Regarding uniform dispersion of microorganisms in organic waste, see JP-A-08-109086 and JP-A-11-347526.
Any of the above can be expected because microorganisms disperse by adhering to wood chips, plastic or metal hollow structure molded products.
However, wood chips absorb water and prevent micropores where microorganisms can hide. In addition, in the case of a molded article of a hollow structure made of plastic or metal, if the hollow structure portion is too large, crushed organic matter enters and exits more and microorganisms are discharged, and if the hollow structure portion is too small, the organic matter causes clogging. It is presumed that the dispersion of microorganisms is not reliable.
In view of these problems, we are reviewing the overall decomposition process to enable more efficient biodegradation by microorganisms.
investigated.

【0009】[0009]

【課題を解決するための手段】上記検討により、まず分
解処理の効率化を図る補助部材として、密閉容器内に有
機物と共に投入して攪拌、混合することでこの有機物の
微生物による生分解を促進するブロックであって、耐摩
耗性を備えた合成樹脂の一体成形品からなり、この一体
成形品は外面に凹凸を形成し、この凹凸により衝突する
有機物に対して点又は線状に破砕力を加えることができ
るようにした生分解促進ブロックを開発した。この生分
解促進ブロックは、主として有機廃棄物の分解処理に用
いるが、性能的には有機物全般に作用できる。
According to the above study, first, as an auxiliary member for improving the efficiency of the decomposition treatment, the organic matter is put into a closed container together with stirring and mixed to promote the biodegradation of the organic matter by microorganisms. The block is made of an integrally molded article of a synthetic resin having abrasion resistance, and the integrally molded article has irregularities formed on an outer surface, and applies a crushing force in a point or linear manner to an organic substance colliding by the irregularities. A biodegradation promoting block was developed. This biodegradation promoting block is mainly used for the decomposition treatment of organic waste, but can act on organic matter in general in performance.

【0010】耐摩耗性を備えた合成樹脂としては、ポリ
アセタール、ナイロン12、ポリプロピレン、ポリカーボ
ネートやFRP等、いわゆるエンジニアリングプラスチッ
クが好ましく、例えば廃棄された自動車用同プラスチッ
クを再生利用できる。外面に凹凸を形成する一体成形品
の構造としては、複数の凹凸からなる多面体や多角柱形
状の成形品があり、とりわけ断面星形の柱状成形品が好
ましい。この凹凸のうち凸部位が、有機物に対して点又
は線状に接触して局部的な破砕力を加える。生分解促進
ブロックは、多数個投入するため、前記点又は線状に加
える破砕力は、各個ばらばらの大きさ及び方向を有し、
これが有機物の微細化に適している。また、凹凸のうち
凹部位は、微生物の付着部位として微生物の分散を助け
る。本発明の生分解促進ブロックは必ずしも中空構造に
する必要はないが、微生物の分散性を高めるには、微生
物が待避して潜り込める部位を確保する意味から、中空
構造を採用しても構わない。
As the synthetic resin having abrasion resistance, so-called engineering plastics such as polyacetal, nylon 12, polypropylene, polycarbonate and FRP are preferable. For example, the same plastic discarded for automobiles can be recycled. Examples of the structure of the integrally molded article having the unevenness on the outer surface include a polyhedron or a polygonal shaped article having a plurality of irregularities, and a columnar shaped article having a star-shaped cross section is particularly preferable. The convex portion of the irregularities comes into contact with the organic substance in a point or linear manner, and applies a local crushing force. The biodegradation accelerating block, because a large number of pieces are introduced, the crushing force applied to the point or the linear shape has a size and a direction of each piece,
This is suitable for miniaturization of organic substances. In addition, the concave portion among the concaves and convexes assists the dispersion of the microorganism as an attachment site of the microorganism. The biodegradation-promoting block of the present invention does not necessarily need to have a hollow structure, but in order to enhance the dispersibility of microorganisms, a hollow structure may be adopted from the viewpoint of securing a site where microorganisms can escape and dive. .

【0011】次に、装置構成を見直して、投入した有機
物を攪拌、混合しながら微生物により生分解する処理装
置であって、投入した有機物を攪拌、混合する攪拌羽根
を内蔵した密閉容器からなり、この密閉容器壁面に断熱
ジャケットを覆設して加温空間を形成し、攪拌羽根の下
り方向及び上り方向それぞれに向けた一対の温風供給口
を前記加温空間に連通して設け、前記加温空間に連通し
ない位置に排気口を設けて、加温空間へ供給する温風に
よって密閉容器全体を加温して間接的に有機物を加温す
ると共に、温風供給口から密閉容器内の有機物に向けて
温風を吹き出して直接的に有機物を加温し、また前記温
風により密閉容器内へ新鮮な空気の供給を図り、発生し
たガス又は古い空気を排気口から排出して一連の空気の
循環経路を構成した生分解処理装置を開発した。
Next, the apparatus configuration is reviewed, and a processing apparatus for performing biodegradation by microorganisms while stirring and mixing the input organic substance, comprising a sealed container having a built-in stirring blade for stirring and mixing the input organic substance, A heating space is formed by covering the heat insulating jacket on the wall surface of the closed container, and a pair of hot air supply ports are provided in communication with the heating space in a downward direction and an upward direction of the stirring blade, respectively. An exhaust port is provided at a position that does not communicate with the warm space, and the entire closed vessel is heated by warm air supplied to the warming space to indirectly heat organic matter. A warm air is blown out to directly heat the organic matter, and a fresh air is supplied into the closed container by the warm air, and a generated gas or old air is discharged from an exhaust port to form a series of air. The circulation path of It has developed a biodegradable processing apparatus.

【0012】加温空間へ温風を送り込む密閉容器全体の
加温は、分解処理中に外部へ逃げる熱を補い、有機廃棄
物の降温を防ぐ意味がある。これに対して、温風供給口
から吹き出す温風は、直接的に有機物を加温する。密閉
容器内で攪拌羽根に巻き込まれるように攪拌、混合され
る有機物は、攪拌羽根回転方向の一方では巻き込んで押
さえ込まれ(下り方向)、他方では巻き込んで持ち上げら
れる(上り方向)。仮に温風供給口が1基のみであれば、
下り方向又は上り方向いずれかに向くことになり、下り
方向と上り方向とで温度差が生じる虞れがある。このた
め、本発明の生分解処理装置では、攪拌羽根の下り方向
及び上り方向それぞれに向けた一対の温風供給口を設
け、攪拌羽根の巻き込みによる有機物の温度低下を招か
ないようにし、もって有機物における温度分布を略均一
にしている。この場合、下り方向では攪拌羽根による有
機物の巻き上げは起こらないが、上り方向では有機物の
跳ね上げの虞れがあるため、温風供給口を高い位置に設
けて有機物による目詰まりを防止できるようにするとよ
い。この結果、下り方向に対する温風供給口と上り方向
に対する温風供給口とは、段違いとなる。
The heating of the entire closed vessel that sends warm air into the heating space has the meaning of supplementing the heat escaping to the outside during the decomposition treatment and preventing the temperature of the organic waste from dropping. On the other hand, the warm air blown out from the warm air supply port directly heats the organic matter. The organic matter to be stirred and mixed so as to be caught by the stirring blade in the closed vessel is caught and held (downward direction) in one of the rotation directions of the stirring blade, and is caught and lifted (upward direction) in the other direction. If there is only one hot air supply port,
It is directed in either the down direction or the up direction, and there is a possibility that a temperature difference occurs between the down direction and the up direction. For this reason, in the biodegradation treatment apparatus of the present invention, a pair of hot air supply ports are provided for the down direction and the up direction of the stirring blade, respectively, so that the temperature of the organic material does not decrease due to the entrainment of the stirring blade, so that the organic material is prevented. Is made substantially uniform. In this case, organic substances are not wound up by the stirring blades in the downward direction, but there is a risk of organic substances jumping up in the upward direction, so that a hot air supply port is provided at a high position to prevent clogging by organic substances. Good to do. As a result, the hot air supply port for the downward direction and the hot air supply port for the upward direction are stepped.

【0013】また、温風供給口から吹き出す温風は、密
閉容器内へ新鮮な空気を送り込む役割を果たし、攪拌羽
根の下り方向及び上り方向それぞれに向けた一対の温風
供給口を設けることで、密閉容器内全域に広く新鮮な空
気を供給できる。生分解を発揮する微生物は好気性菌で
あり、生分解によって発生する二酸化炭素や水蒸気を適
宜排出し、代わって新鮮な空気を送り込むことで、微生
物の活発な働きを確保できる。本発明では、温風供給口
と排気口とを組み合わせることで、一連の空気の循環経
路を構成し、微生物の活発な働きを確保できる換気を実
現する。このため、温風の供給は加圧、排気は吸引によ
る負圧にすると、より好ましい。排気は同時に水蒸気を
排出するが、液化して溜まる水については、別途密閉容
器に排水口を設けて排出するとよい。
[0013] The hot air blown out from the hot air supply port serves to feed fresh air into the closed container, and is provided with a pair of hot air supply ports directed to the downward direction and the upward direction of the stirring blade. In this way, fresh air can be widely supplied to the whole area in the closed container. Microorganisms that exhibit biodegradation are aerobic bacteria, and the active function of the microorganisms can be ensured by appropriately discharging carbon dioxide and water vapor generated by biodegradation and sending fresh air in place. In the present invention, a combination of the hot air supply port and the exhaust port constitutes a series of air circulation paths, and realizes ventilation that can ensure active action of microorganisms. For this reason, it is more preferable that the supply of the warm air be pressurized and the exhaust be a negative pressure by suction. Exhaust simultaneously discharges water vapor, but water that liquefies and accumulates may be discharged by providing a drainage port separately in a closed container.

【0014】こうして、上記生分解処理装置の密閉容器
に本発明の生分解促進ブロックと共に有機廃棄物を投入
し、密閉容器全体の加温と温風の吹き出しとにより間接
的及び直接的に有機廃棄物を加温して、この有機廃棄物
の温度を微生物の繁殖に適した温度範囲に維持した状態
で、生分解促進ブロックが外面によって有機廃棄物を物
理的に粉砕しながらこの生分解促進ブロックに付着して
微生物が均一に分散することで、微生物による有機廃棄
物の生分解を促進する有機廃棄物分解処理方法を実現で
きる。本発明の生分解処理装置と生分解促進ブロックと
の組み合わせにより、生分解処理に必要な条件(1),(2)
及び(3)がすべて充足され、従来に比べて短時間でほぼ
完全な生分解が可能となる。生分解促進ブロックは、連
続的な使用においても磨耗することなく、定期的に水洗
して繰り返し使用する。
Thus, the organic waste is put into the sealed container of the biodegradation treatment apparatus together with the biodegradation promoting block of the present invention, and the organic waste is indirectly and directly indirectly heated by warming the whole sealed container and blowing out hot air. The biodegradation-promoting block heats the material and maintains the temperature of the organic waste in a temperature range suitable for the propagation of microorganisms. By dispersing the microorganisms uniformly on the organic waste, an organic waste decomposition treatment method that promotes biodegradation of organic wastes by the microorganisms can be realized. By the combination of the biodegradation treatment device of the present invention and the biodegradation promoting block, the conditions required for biodegradation treatment (1), (2)
And (3) are all satisfied, and almost complete biodegradation is possible in a shorter time than before. The biodegradation-promoting block is periodically washed with water and used repeatedly without abrasion even in continuous use.

【0015】[0015]

【発明の実施の形態】以下、本発明の実施形態につい
て、図を参照しながら説明する。図1は本発明の一例を
示す生分解処理装置の部分破断正面図、図2は同生分解
処理装置の処理開始前を表す断面図、図3は同生分解処
理装置の密閉容器1内に予め投入しておく生分解促進ブ
ロック2の一例を示す斜視図、図4は処理中を表す図2
相当断面図であり、図5は処理完了を表す図2相当断面
図である。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a partially cutaway front view of a biodegradation apparatus showing an example of the present invention, FIG. 2 is a cross-sectional view of the biodegradation apparatus before starting processing, and FIG. FIG. 4 is a perspective view showing an example of the biodegradation accelerating block 2 which is put in advance, and FIG.
FIG. 5 is a sectional view corresponding to FIG. 2 showing the completion of the processing.

【0016】本例に示す生分解処理装置は、外観や基本
的な構造は従来見られる同様の装置と変わりはない。生
分解処理装置は、図1又は図2に見られるように、処理
対象となる有機廃棄物3と生分解を促進する生分解促進
ブロック2(図3参照)とを投入する密閉容器1を中心に
構成し、図示を省略するが、回転軸5の電源部又は動力
部、制御部や脱臭装置等を付設する。密閉容器1は、攪
拌羽根4を半径方向に突設した回転軸5を内蔵し、底部
6は前記回転羽根4の回転軌跡外縁に沿う円弧状に形成
している。密閉容器1上部前面には投入口7を、同密閉
容器1下部背面には排出口8を設けている。投入口7か
らは、有機廃棄物3や生分解促進ブロック2を投入す
る。有機廃棄物3は生分解を受けて殆ど残らないが、定
期的に生分解促進ブロック2を回収する際に排出口8を
利用する。
The appearance and basic structure of the biodegradation treatment apparatus shown in this embodiment are the same as those of a similar apparatus which has been conventionally seen. As shown in FIG. 1 or FIG. 2, the biodegradation treatment apparatus mainly includes a sealed container 1 into which an organic waste 3 to be treated and a biodegradation promoting block 2 (see FIG. 3) for promoting biodegradation are charged. Although not shown, a power supply unit or a power unit of the rotating shaft 5, a control unit, a deodorizing device, and the like are additionally provided. The closed vessel 1 has a built-in rotary shaft 5 in which a stirring blade 4 is protruded in a radial direction, and a bottom portion 6 is formed in an arc shape along the outer edge of the rotation locus of the rotary blade 4. An inlet 7 is provided on the upper front surface of the closed container 1 and an outlet 8 is provided on the lower rear surface of the closed container 1. The organic waste 3 and the biodegradation accelerating block 2 are introduced through the inlet 7. Although the organic waste 3 hardly remains after undergoing biodegradation, the outlet 8 is used when the biodegradation promoting block 2 is periodically collected.

【0017】密閉容器1は、壁面9に対して断熱ジャケ
ット10を覆設しており、内部に貫通する排気口11、排水
口12及び回転軸5と、投入口7及び排出口8を除く範囲
に加温空間Sを形成している。この加温空間Sには外部
の加熱送風部(図示略)より温風供給パイプ13を通じて温
風Fが供給され、加温空間S全域を加温して、密閉容器
1に投入した有機廃棄物3を間接的に加温する。また、
温風Fは密閉容器1側面に設けた一対の温風供給口14,1
5から吹き出し、密閉容器1に投入した有機廃棄物3を
直接的に加温する。本例の密閉容器1における温風供給
口14,15は、図2に見られるように、投入口7下縁に沿
って並べた下位供給口14と、対向面上方に並べた上位供
給口15とからなる。回転軸5は投入口7に向かって回転
しているので、下位供給口14が攪拌羽根4の下り方向、
上位供給口15が攪拌羽根4の上り方向に対応している。
下位供給口14には温風Fの吹出方向を斜め下に規制する
偏向板16を付設し、上位供給口15には攪拌羽根4が跳ね
上げた有機廃棄物3が飛び込まないように仕切板17を内
部に設け、併せて温風Fの吹出方向を斜め下に規制して
いる。
The closed container 1 has a heat insulating jacket 10 covered on a wall surface 9, and a range excluding an exhaust port 11, a drain port 12 and a rotating shaft 5 penetrating therethrough, and an inlet 7 and an outlet 8. To form a heating space S. Hot air F is supplied to the heating space S from an external heating air blower (not shown) through a hot air supply pipe 13, and the entire heating space S is heated, and the organic waste put into the closed container 1 is heated. Heat 3 indirectly. Also,
The hot air F is supplied to a pair of hot air supply ports 14 and 1 provided on the side of the closed container 1.
The organic waste 3 blown out from 5 and charged into the closed container 1 is directly heated. As shown in FIG. 2, the hot air supply ports 14 and 15 in the closed container 1 of the present embodiment include a lower supply port 14 arranged along the lower edge of the inlet 7 and an upper supply port 15 arranged above the facing surface. Consists of Since the rotating shaft 5 is rotating toward the charging port 7, the lower supply port 14 is in the downward direction of the stirring blade 4,
The upper supply port 15 corresponds to the upward direction of the stirring blade 4.
The lower supply port 14 is provided with a deflecting plate 16 for restricting the blowing direction of the warm air F obliquely downward, and the upper supply port 15 is provided with a partition plate 17 for preventing the organic waste 3 jumped up by the stirring blades 4 from jumping into the upper supply port 15. Is provided inside, and the blowing direction of the warm air F is also restricted obliquely downward.

【0018】本例に用いる生分解促進ブロック2は、図
3に見られるような、ギア又は星形状断面を有する中空
の柱体構造で、耐磨耗性を備えたエンジニアリングプラ
スチックにより一体成形している。外面に突出する歯18
(凸部位)が有機廃棄物に衝突すると線状に破砕力を加え
て、生分解を受けてもろくなりつつある有機廃棄物を破
砕し、微細化していく。微生物は、歯と歯との間19(凹
部位)に付着したり、中空構造を形作る横断孔20内に潜
り込んで、生分解促進ブロック2の攪拌と共に密閉容器
内部全域へ略均一に拡散する。この生分解促進ブロック
2は、小型であるほど有機廃棄物との接触延べ面積が大
きくなるので好ましいが、小さすぎると前記破砕力が小
さくなる。本発明においては、生分解性ブロック2の構
造が重要であるため、大きさについて限定はないが、お
よそ外形7〜20mm、長さ7〜20mmを例示できる。また、
材料となるエンジニアリングプラスチックは、新規に製
造してもよいし、廃材利用、例えば廃車から回収された
同素材を再利用できる。
The biodegradation promoting block 2 used in this embodiment is a hollow columnar structure having a gear or a star-shaped cross section as shown in FIG. 3, and is integrally formed of a wear-resistant engineering plastic. I have. Externally projecting teeth 18
When the (convex portion) collides with the organic waste, the crushing force is applied linearly to crush the organic waste which is undergoing biodegradation and becoming fragile and becomes finer. Microorganisms adhere to the teeth 19 between the teeth (recessed positions) or sneak into the transverse holes 20 forming a hollow structure, and are diffused substantially uniformly throughout the inside of the closed container with stirring of the biodegradation promoting block 2. It is preferable that the biodegradation promoting block 2 is small, because the total contact area with the organic waste becomes large. However, if it is too small, the crushing force becomes small. In the present invention, since the structure of the biodegradable block 2 is important, the size is not limited, but may be about 7 to 20 mm in outer shape and 7 to 20 mm in length. Also,
The engineering plastic used as the material may be newly manufactured, or may be reused, for example, the same material recovered from a scrapped vehicle.

【0019】次に、本発明による有機廃棄物3の分解処
理の手順について説明する。まず、図2に見られるよう
に、予め多数の生分解促進ブロック2を投入しておいた
密閉容器1内に対し、投入口7から処理対象となる有機
廃棄物3を投入する。本発明による生分解は、有機廃棄
物3の種類を問わないので、ホテル、旅館、飲食店や家
庭から排出される生ごみ、有機産業廃棄物、海産物残
渣、下水汚泥、糞尿汚泥らを混在させて処理できる。生
分解を担う微生物は、有機廃棄物3自身に付着していた
り、大気中に浮遊しているので、補給する必要はない。
本発明では、こうした微生物が最大限能力を発揮できる
環境を作り出し、有機廃棄物3を短時間に生分解処分す
る。
Next, the procedure of the decomposition treatment of the organic waste 3 according to the present invention will be described. First, as shown in FIG. 2, the organic waste 3 to be treated is charged from the charging port 7 into the sealed container 1 in which a large number of biodegradation promoting blocks 2 have been charged in advance. Since the biodegradation according to the present invention does not depend on the type of the organic waste 3, it mixes garbage discharged from hotels, inns, restaurants and homes, organic industrial waste, marine residues, sewage sludge, and manure sludge. Can be processed. Microorganisms responsible for biodegradation do not need to be replenished because they attach to the organic waste 3 itself or float in the atmosphere.
In the present invention, an environment in which such microorganisms can exert their maximum capacity is created, and the organic waste 3 is biodegraded and disposed in a short time.

【0020】投入口7を閉鎖した後、図4に見られるよ
うに攪拌羽根4を回転させて、生分解促進ブロック2と
有機廃棄物3とが混在する状態で攪拌、混合していく。
同時に、温風供給パイプ13から加温空間Sへ温風Fが供
給され、一対の温風供給口14,15から有機廃棄物3に向
けて温風Fを吹出すことで、間接的及び直接的に有機廃
棄物3を加温する。温風供給口14,15からの温風Fの吹
出しは新鮮な空気の供給の意味も有するが、主たる目的
は有機廃棄物3の加温である。本発明の生分解処理にお
いて利用する微生物は、概ね好気性高温菌であり、生分
解に必要な環境温度は40〜70℃、好ましくは45〜55℃で
ある。このため、温風Fは専ら前記環境温度を実現する
のに用い、別途密閉容器1に吸気口を設けて、新鮮な空
気の補充を図るようにしてもよい。
After the inlet 7 is closed, the stirring blades 4 are rotated as shown in FIG. 4 to stir and mix the biodegradation promoting block 2 and the organic waste 3 in a mixed state.
At the same time, the warm air F is supplied from the warm air supply pipe 13 to the heating space S, and the warm air F is blown out from the pair of warm air supply ports 14 and 15 toward the organic waste 3, thereby indirectly and directly. The organic waste 3 is heated. The blowing of the warm air F from the warm air supply ports 14 and 15 also has the meaning of supplying fresh air, but the main purpose is to heat the organic waste 3. The microorganism used in the biodegradation treatment of the present invention is generally an aerobic thermophilic bacterium, and the environmental temperature required for biodegradation is 40 to 70 ° C, preferably 45 to 55 ° C. For this reason, the warm air F may be used exclusively for realizing the above-mentioned environmental temperature, and an air inlet may be separately provided in the closed container 1 so as to replenish fresh air.

【0021】図4から明らかなように、有機廃棄物3及
び生分解促進ブロック2は、攪拌羽根4の攪拌により、
攪拌羽根4の下り方向で圧縮されて低く、同上り方向で
盛り上がって高くなる。この結果、一対の温風供給口1
4,15の有機廃棄物3に対する距離はほぼ等しくなり、加
温作用も等しくできる。このように、温風供給口14,15
に高低差を設けることは、密閉容器1内での温度分布を
均一にする。このような環境のもと、有機廃棄物3は下
位供給口14からの温風Fによって直接的に加温され、攪
拌羽根4により下り方向に押し込まれる。加温空間Sに
よる間接的な加温は有機廃棄物3の温度低下を防ぎ、持
続的な微生物の生分解を助ける。しかし、下位供給口14
から遠くなる位置、例えば攪拌羽根4の上り方向では有
機廃棄物3の温度低下が起きやすい。そこで、上位供給
口15から温風Fを吹出して前記温度低下を防ぐ。本発明
では、このようにして、密閉容器内1の温度分布は略均
一に保ち、生分解に適した環境を構築している。
As is clear from FIG. 4, the organic waste 3 and the biodegradation promoting block 2 are stirred by the stirring blades 4.
The stirring blade 4 is compressed in the downward direction and low, and rises and rises in the upward direction. As a result, a pair of hot air supply ports 1
The distances of the organic wastes 3 and 4 to the organic waste 3 are substantially equal, and the heating action can be equalized. Thus, the hot air supply ports 14, 15
Providing a difference in height makes the temperature distribution in the closed vessel 1 uniform. Under such an environment, the organic waste 3 is directly heated by the warm air F from the lower supply port 14 and pushed down by the stirring blade 4. The indirect heating by the heating space S prevents the temperature of the organic waste 3 from lowering and helps the continuous biodegradation of microorganisms. However, the lower supply port 14
The temperature of the organic waste 3 is apt to decrease at a position farther away from, for example, the ascending blade 4. Therefore, the lowering of the temperature is prevented by blowing out the warm air F from the upper supply port 15. In the present invention, the temperature distribution in the closed container 1 is maintained substantially uniform in this way, and an environment suitable for biodegradation is established.

【0022】有機廃棄物3の生分解処理を迅速にするも
うひとつの要素は、生分解促進ブロック2による物理的
な破砕である。微生物は、有機廃棄物3を生分解して二
酸化炭素と水(多くは水蒸気として発生する)とに生分解
するが、この生分解はミクロ的なものであり、単純に生
分解を実施すると、有機廃棄物3全体を生分解して消去
してしまうには時間がかかる。そこで、本発明では、生
分解促進ブロック2の外面に設けた凹凸18,19により有
機廃棄物3を物理的に破砕し、ミクロ的な生分解によっ
て逐次有機廃棄物3を消去できるようにしている。こう
して、本発明によれば、およそ6時間程度で投入した有
機廃棄物を生分解して、ほとんど固形物が残らない程度
に消去できる。
Another factor that speeds up the biodegradation of the organic waste 3 is physical crushing by the biodegradation promoting block 2. Microorganisms biodegrade organic waste 3 and biodegrade into carbon dioxide and water (often generated as water vapor). This biodegradation is microscopic, and if biodegradation is simply carried out, It takes time to biodegrade and erase the entire organic waste 3. Therefore, in the present invention, the organic waste 3 is physically crushed by the unevennesses 18 and 19 provided on the outer surface of the biodegradation promoting block 2 so that the organic waste 3 can be sequentially erased by micro biodegradation. . Thus, according to the present invention, the organic waste input in about 6 hours can be biodegraded and erased to such an extent that almost no solid remains.

【0023】処理後は、図5に見られるように、密閉容
器1内には生分解促進ブロック2のみが残り、二酸化炭
素及び水蒸気は排気口11から、水は排水口12からそれぞ
れ排出される。生分解に適した環境維持のため、温風供
給口14,15から新鮮な空気を供給するのに対して、排気
口11には吸引装置を接続し、一連の空気の循環経路を構
成するとよい。また、生分解促進ブロック2は吸水性を
有していないため、有機廃棄物3が出す汚水等を吸着す
ることなく、この汚水も生分解してしまうため、例えば
木片を利用した生分解に比べて異臭を発する虞れが少な
い。しかし、当初より異臭を発する有機廃棄物も処理す
ることも考えられるから、排気口11に対しては脱臭装置
(図示略)を接続するとよい。
After the treatment, as shown in FIG. 5, only the biodegradation promoting block 2 remains in the closed vessel 1, and carbon dioxide and water vapor are discharged from the exhaust port 11 and water is discharged from the drain port 12, respectively. . In order to maintain an environment suitable for biodegradation, fresh air is supplied from the hot air supply ports 14 and 15, while a suction device is connected to the exhaust port 11 and a series of air circulation paths may be configured. . In addition, since the biodegradation promoting block 2 does not have water absorption, the sewage is also biodegraded without adsorbing the sewage and the like generated by the organic waste 3. There is little risk of giving off odor. However, it is conceivable to treat organic waste that emits an odor from the beginning.
(Not shown) should be connected.

【0024】[0024]

【発明の効果】本発明により、異臭を発生させることな
く、短時間に有機廃棄物の生分解処理を実現できるよう
になる。上述した通り、生分解処理は有機廃棄物を二酸
化炭素と水とに分解するため、二次処理すべき残渣もな
く、廃棄物処理手段としては優れている。しかも、従来
装置では処理時間が比較的長く必要としていたために異
臭を発していたが、本発明では処理時間を大幅に短縮で
きるのでほとんど異臭を発生させずに済む利点がある。
これらは、物理的破砕能力を付加した生分解促進ブロッ
クと、適切な環境、とりわけ温度維持を図る生分解処理
装置との組み合わせによるところが大きい。それぞれ、
単独にて利用可能であるが、本発明は両者を併用するこ
とによって、最も理想的な有機廃棄物の生分解処理を実
現する。
According to the present invention, the biodegradation of organic waste can be realized in a short time without generating an off-flavor. As described above, the biodegradation treatment decomposes organic waste into carbon dioxide and water, so there is no residue to be subjected to secondary treatment, and it is an excellent waste treatment means. In addition, in the conventional apparatus, the processing time was required relatively long, so that an unpleasant odor was generated. However, in the present invention, since the processing time can be greatly reduced, there is an advantage that almost no unpleasant odor is generated.
These are largely due to the combination of a biodegradation accelerating block with added physical crushing ability and a biodegradation treatment device for maintaining an appropriate environment, especially a temperature. Respectively,
Although it can be used alone, the present invention realizes the most ideal biodegradation treatment of organic waste by using both together.

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

【図1】本発明の一例を示す生分解処理装置の部分破断
正面図である。
FIG. 1 is a partially broken front view of a biodegradation treatment apparatus showing an example of the present invention.

【図2】同生分解処理装置の処理開始前を表す断面図で
ある。
FIG. 2 is a cross-sectional view illustrating a state before the start of processing by the biodegradation processing apparatus.

【図3】同生分解処理装置の密閉容器内に予め投入して
おく生分解促進ブロックの一例を示す斜視図である。
FIG. 3 is a perspective view showing an example of a biodegradation accelerating block previously charged in a closed container of the biodegradation treatment apparatus.

【図4】処理中を表す図2相当断面図である。FIG. 4 is a sectional view corresponding to FIG. 2 showing a state during processing.

【図5】処理完了を表す図2相当断面図である。FIG. 5 is a sectional view corresponding to FIG. 2, showing the completion of processing.

【符号の説明】[Explanation of symbols]

1 密閉容器 2 生分解促進ブロック 3 有機廃棄物 4 攪拌羽根 14 下位供給口(温風供給口) 15 上位供給口(温風供給口) S 加温空間 F 温風 DESCRIPTION OF SYMBOLS 1 Closed container 2 Biodegradation promotion block 3 Organic waste 4 Stirrer blade 14 Lower supply port (hot air supply port) 15 Upper supply port (hot air supply port) S Heating space F Hot air

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D004 AA03 BA04 CA04 CA15 CA19 CA48 CB04 CB06 CB13 CB28 CB36 CB43 CC08 DA02 DA06 4D067 CG06 DD03 EE32 EE47 GA17 GB01 4G037 CA01 CA03 EA03 4G078 AA04 AB20 BA01 CA01 DA01 EA03 EA13  ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 4D004 AA03 BA04 CA04 CA15 CA19 CA48 CB04 CB06 CB13 CB28 CB36 CB43 CC08 DA02 DA06 4D067 CG06 DD03 EE32 EE47 GA17 GB01 4G037 CA01 CA03 EA03 4G078 AA04 AB20 BA01 CA01 DA01

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 密閉容器内に有機物と共に投入して攪
拌、混合することで該有機物の微生物による生分解を促
進するブロックであって、耐摩耗性を備えた合成樹脂の
一体成形品からなり、該一体成形品は外面に凹凸を形成
し、該凹凸により衝突する有機物に対して点又は線状に
破砕力を加えることができるようにしてなる生分解促進
ブロック。
1. A block for promoting biodegradation of an organic substance by microorganisms by introducing the organic substance into a closed container together with stirring and mixing, and comprises an integrally molded article of a synthetic resin having wear resistance. A biodegradation accelerating block in which the integrally molded article has irregularities formed on an outer surface thereof so that a crushing force can be applied to organic substances colliding with the irregularities in a point or linear manner.
【請求項2】 投入した有機物を攪拌、混合しながら微
生物により生分解する処理装置であって、投入した有機
物を攪拌、混合する攪拌羽根を内蔵した密閉容器からな
り、該密閉容器壁面に断熱ジャケットを覆設して加温空
間を形成し、攪拌羽根の下り方向及び上り方向それぞれ
に向けた一対の温風供給口を前記加温空間に連通して設
け、前記加温空間に連通しない位置に排気口を設けて、
加温空間へ供給する温風によって密閉容器全体を加温し
て間接的に有機物を加温すると共に、温風供給口から密
閉容器内の有機物に向けて温風を吹き出して直接的に有
機物を加温し、また前記温風により密閉容器内へ新鮮な
空気の供給を図り、発生したガス又は古い空気を排気口
から排出して一連の空気の循環経路を構成してなる生分
解処理装置。
2. A processing apparatus for biodegrading an inputted organic substance by a microorganism while stirring and mixing the same, comprising a sealed container having a built-in stirring blade for stirring and mixing the inputted organic substance, wherein a heat insulating jacket is provided on a wall surface of the closed container. To form a heating space, and a pair of hot air supply ports respectively directed to the down direction and the up direction of the stirring blade are provided in communication with the heating space, and at a position not communicating with the heating space. Provide an exhaust port,
The whole closed container is heated by the warm air supplied to the heating space to indirectly heat the organic matter, and the warm air is blown out from the hot air supply port toward the organic matter in the closed vessel to directly remove the organic matter. A biodegradation treatment apparatus configured to heat and supply fresh air into the closed container by the hot air and discharge generated gas or old air from an exhaust port to form a series of air circulation paths.
【請求項3】 請求項2記載の生分解処理装置の密閉容
器に請求項1記載の生分解促進ブロックと共に有機廃棄
物を投入し、密閉容器全体の加温と温風の吹き出しとに
より間接的及び直接的に有機廃棄物を加温して、該有機
廃棄物の温度を微生物の繁殖に適した温度範囲に維持し
た状態で、生分解促進ブロックが外面によって有機廃棄
物を物理的に粉砕しながら該生分解促進ブロックに付着
して微生物が均一に分散することで、微生物による有機
廃棄物の生分解を促進する有機廃棄物分解処理方法。
3. An organic waste together with the biodegradation accelerating block according to claim 1 is charged into the closed container of the biodegradation treatment apparatus according to claim 2, and indirectly by heating the whole closed container and blowing out hot air. And directly heating the organic waste, while maintaining the temperature of the organic waste in a temperature range suitable for the propagation of microorganisms, the biodegradation promoting block physically pulverizes the organic waste by the outer surface. An organic waste decomposition treatment method that promotes biodegradation of organic waste by microorganisms by adhering to the biodegradation promoting block while uniformly dispersing the microorganisms.
JP2000206440A 2000-07-07 2000-07-07 Biodegradation treatment apparatus and organic waste decomposition treatment method using them Expired - Fee Related JP3946939B2 (en)

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JP3946939B2 JP3946939B2 (en) 2007-07-18

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004202413A (en) * 2002-12-26 2004-07-22 Kiyomoto Bio Co Ltd Method and apparatus for recycling treatment of organic waste
JP2013517933A (en) * 2010-01-28 2013-05-20 ビューラー・アクチエンゲゼルシャフト Mixer with splashing surface
JP2013176408A (en) * 2012-02-28 2013-09-09 Ryu Shinke Toxic substance decomposition treatment method of waste oil, and decomposition treatment plant of the same
CN116137985A (en) * 2023-02-09 2023-05-23 中国热带农业科学院热带作物品种资源研究所 Soil treatment equipment and treatment method thereof

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004202413A (en) * 2002-12-26 2004-07-22 Kiyomoto Bio Co Ltd Method and apparatus for recycling treatment of organic waste
JP2013517933A (en) * 2010-01-28 2013-05-20 ビューラー・アクチエンゲゼルシャフト Mixer with splashing surface
JP2013176408A (en) * 2012-02-28 2013-09-09 Ryu Shinke Toxic substance decomposition treatment method of waste oil, and decomposition treatment plant of the same
CN116137985A (en) * 2023-02-09 2023-05-23 中国热带农业科学院热带作物品种资源研究所 Soil treatment equipment and treatment method thereof
CN116137985B (en) * 2023-02-09 2023-08-11 中国热带农业科学院热带作物品种资源研究所 Soil treatment equipment and treatment method thereof

Also Published As

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