JP2000176428A - Disposal of garbage or the like - Google Patents

Disposal of garbage or the like

Info

Publication number
JP2000176428A
JP2000176428A JP10377878A JP37787898A JP2000176428A JP 2000176428 A JP2000176428 A JP 2000176428A JP 10377878 A JP10377878 A JP 10377878A JP 37787898 A JP37787898 A JP 37787898A JP 2000176428 A JP2000176428 A JP 2000176428A
Authority
JP
Japan
Prior art keywords
garbage
fermentation
tanks
treated material
circulated
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10377878A
Other languages
Japanese (ja)
Inventor
Kazuhiko Takemura
一彦 竹村
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.)
TAKEMURA KK
Original Assignee
TAKEMURA KK
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 TAKEMURA KK filed Critical TAKEMURA KK
Priority to JP10377878A priority Critical patent/JP2000176428A/en
Publication of JP2000176428A publication Critical patent/JP2000176428A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Fertilizers (AREA)

Abstract

PROBLEM TO BE SOLVED: To rationally and continuously dispose of garbage or the like to obtain compost of stable quality by circulating material that has subjected to fermentation treatment (treated material) in treating processes successively and mixing garbage or the like newly fed with the treated material circulated successively. SOLUTION: Fermentation tanks 4, 5 form upper and lower two tanks and material whose fermentation has made progress and which has larger heat generation passes through the lower stage. Within the upper and lower tanks, agitating shafts 6, 7 for both agitation and transfer are provided respectively. To the agitating shafts 6, 7, blades are fitted, and the shafts 6, 7 are driven by motors 8, 9 for inverters respectively. To the upper and lower tanks, compressed air is fed from a compressor 10 through air feeding pipes 12, 11 respectively. Exhaust air containing vapor is passed through discharge pipes 14, 13 and is finally led to a heat exchanger 15 while radiating heat and heats the intake air, and after that, it is discharged to the outside. The treated material is taken out from a discharge port 16. Here, the garbage or the like is subjected to fermentation treatment in the fermentation tanks 4, 5, and the treated material is circulated in treating processes successively, and newly fed garbage or the like is mixed with the treated material circulated successively.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【考案に関連する技術の現状】環境問題は極めて今日的
な大問題であるが、就中毎日必ず排出される生ごみは日
常の生活に直結しており、その処理には諸々の課題が課
せられている。即ち、焼却には排出ガスや焼却残渣など
の問題、堆肥化には堆肥化の技術そのものや用途先の問
題など種々あり、容易に先行きが見通せない状況であ
る。しかし、にも拘らずその解決は極めて緊急を要す
る。では先ず、何を目指すかであるが、極めて合理的に
考えるならば、焼却処理が今日の地球的時流に逆らうも
のである事は自明であり、堆肥化以外の選択肢は思い浮
かばないが、その堆肥化処理の進展を妨げているのは一
体何か。全ては、末梢的な考えに囚われた稚拙な技術そ
のものに由来すると考える。低コストで生ごみを処理し
堆肥を作る技術は、未確立である。現在の、生ごみから
堆肥を作る試みの多くは成功と言い難い状態で、堆肥と
称して堆肥で無い点は共通している。それは堆肥より肥
効成分を多く含んだ肥料と言うべき物で、問題を理解し
ていない結果である。肥料3要素の1種以上を含有すれ
ば、肥料と評価できるが、生ごみの中身は千差万別、日
毎にも変化する。組成が不定の生ごみを原料とすれば、
肥効成分も又不定になる。つまり、生ごみから肥効成分
を規定した肥料を作るのは至難の技なのである。こうし
た試みの所産は、本来最も合理的な処理方法である筈の
生ごみ堆肥化に手法としての疑念を抱かせる怖れさえあ
る点で罪深いと断ぜざるを得ない。生ごみは全て有機物
であり、又、そうあるべく厳格な分別が必要であるが、
然して生ごみを放置すれば、その終着点は腐植質と称さ
れる多様で且つ比較的に安定な物質であり、多くが腐植
質に変換された時点では、異なる有機物構成で出発して
も出発時の構成に拘らずほゞ同じ性質のものが出来る。
即ち、充分な醗酵に伴う分解合成を経て到達するのが堆
肥であり、農業に安心して使用できるのである。この品
質こそ堆肥化が目指すべき品質であり、その為の技術が
目指すべき目標として競われなければならないのであ
る。因に、腐植質は地中で徐々に分解されて植物の成長
に不可欠な種々の成分を供給する。それが堆肥の役割で
あり、元肥と称される所以でもある。腐植質は土壌中で
刻々と消耗されるから不断の供給が必要である。腐植質
が不足すれば植物は環境の影響を過敏に受け、病害虫に
も侵され易い事が、事実として認識されつつあるが、一
方で堆肥の入手が極めて難しいのが現実である。生ごみ
を堆肥に加工して国内の全農地に配分することになれ
ば、少なくとも、生ごみ廃棄に関する諸問題と、堆肥不
足の一部は解決出来るであろう。以下に述べる方法は機
械装置を用いる生ごみ堆肥化処理の基本であり、究極の
合理化を計るものである。
[Current state of technology related to the invention] Environmental problems are extremely large problems today, but the garbage that is always discharged every day is directly connected to daily life, and various problems are imposed on its disposal. Have been. In other words, incineration has various problems such as exhaust gas and incineration residues, and composting has various problems such as composting technology itself and applications, and it is difficult to foresee the future. Nevertheless, the solution is extremely urgent. First of all, what we aim for is, if we think very reasonably, it is self-evident that incineration is against today's global trends, and there are no options other than composting. What is hindering the progress of composting? I think that everything comes from the poor technique itself, trapped in peripheral ideas. The technology for processing garbage and composting at low cost has not been established. Many of the current attempts to make compost from garbage are unlikely to be successful, and they have in common that compost is not a compost. It is a fertilizer that contains more fertilizer than compost, and is a result of not understanding the problem. Fertilizers can be evaluated as fertilizers if they contain one or more of the three elements, but the contents of garbage vary widely and every day. If garbage of indeterminate composition is used as raw material,
The fertilizing ingredients also become undefined. In other words, it is a very difficult technique to make fertilizers with specified fertilizer components from garbage. The fruits of these attempts have to be deemed guilty in that there is even a fear that they may cast doubt on garbage composting, which should be the most rational treatment method in nature. All garbage is organic and requires strict separation as much as possible,
However, if garbage is left untreated, its end point is a diverse and relatively stable substance called humus, and when most of it is converted to humus, it can start with a different organic matter composition Regardless of the composition of the time, almost the same properties can be obtained.
In other words, compost arrives through decomposition and synthesis accompanied by sufficient fermentation, and can be used safely in agriculture. This quality is the quality that composting should aim for, and the technology for that must be competed as a target to be aimed at. By the way, humus is gradually decomposed in the ground to supply various components essential for plant growth. That is the role of compost, and that's why it is called the original manure. Humus is constantly depleted in the soil and requires constant supply. It is becoming increasingly recognized that plants lack humic substances, are sensitive to the environment and are easily attacked by pests. However, it is actually difficult to obtain compost. Processing food waste into compost and allocating it to all agricultural land in the country would at least solve some of the problems associated with waste disposal and some compost shortages. The method described below is the basis of the garbage composting process using mechanical equipment and is intended for ultimate rationalization.

【考案が解決せんとする課題】i 生ごみ処理に際して
の難問の第一は臭気の発生である。 ii 次いでは醗酵に使う菌類の保持材を大量に必要と
するため効率が極端に低い問題があり、巨大な容積で少
量の処理しか出来ない。大量の菌類保持材も時々入替え
る必要があり、取出す菌類保持材と生ごみの混合物も生
ごみである。堆肥と称しても未分解有機物を多く含む。 iii 処理後の容積を小さくする事が最大の課題であ
るが、未達成である。 iv 更に、醗酵を促進させるために大量の熱エネルギ
ーを必要とする。 v 処理物自体がそのままでは使用できず、ゴミであ
る。ゴミをゴミに加工したのでは、ゴミ処理にならな
い。生ごみの組成に関係なく、一定品質の実用に耐える
物を作る。
[Problem to be Solved by the Invention] i The first problem in processing garbage is the generation of odor. ii Next, there is a problem that the efficiency is extremely low because a large amount of fungi holding material to be used for fermentation is required, and only a small amount of processing can be performed in a huge volume. A large amount of fungus holding material also needs to be replaced from time to time, and the mixture of fungus holding material and garbage to be taken out is also garbage. Even if it is called compost, it contains a lot of undecomposed organic matter. iii The biggest issue is to reduce the volume after processing, but it has not been achieved yet. iv Furthermore, a large amount of heat energy is required to promote fermentation. v The processed material itself cannot be used as it is and is garbage. Processing garbage into garbage does not result in garbage disposal. Regardless of the composition of the garbage, we will make things that can withstand constant quality and practical use.

【課題を解決するための手段】生ごみを醗酵処理する装
置を想定しよう。
An apparatus for fermenting garbage is assumed.

【課題のi】本案に拠れば、処理物は内部で徐々に循環
しやがて新規の生ごみを受け入れ混合されるが、この時
の処理物には既に消臭作用がある。生ごみも、腐植質に
近い状態になっていれば消臭効果を発揮する事が実験で
確認されている。本案はこの点を積極的に活用する為
に、内部で処理物を循環させ、消臭に役立て、いるので
ある。尚、生ごみの排出場所でも腐植質を少量添加すれ
ば、以降生ごみから発生する悪臭を完全に一掃できる事
は先に実用新案として提案したところである。
According to the present invention, the processed material circulates gradually inside, and then accepts and mixes new garbage, but at this time, the processed material already has a deodorizing effect. Experiments have shown that garbage also exhibits a deodorizing effect if it is close to humus. In order to make good use of this point, the present invention circulates the processed material inside and uses it for deodorization. It has been proposed earlier as a utility model that the addition of a small amount of humus to the place where garbage is discharged can completely eliminate the odor generated from the garbage thereafter.

【課題のii】ある段階の処理物には醗酵に使用する菌
類が大量に存在するから、そのまま新規に投入した生ご
みの醗酵用菌類に使用する事が出来る。従って、循環す
る処理物は醗酵用菌類補給の役目も果たしており、巷間
に多くある菌類保持材を必要とするものに比べて遙に優
れている。
Ii) Since a large amount of fungi to be used for fermentation is present in the processed product at a certain stage, it can be used as it is for newly added garbage for fermentation. Therefore, the circulating treated material also plays a role in replenishing fungi for fermentation, and is far superior to those requiring a fungus-retaining material, which is widely available.

【課題のiii】生ごみは醗酵処理する事により体積が
減少する。醗酵が進む程に、減少割合は小さくなる。原
料にも依るが、水分蒸発等で最終的には投入時体積の1
0%以下になり、元生ごみもこの頃には良好な堆肥とし
て利用できる状態になる。
Iii) The volume of garbage is reduced by fermentation. As fermentation progresses, the rate of decrease decreases. Although it depends on the raw materials, the final volume at the time of injection is 1
It becomes 0% or less, and raw garbage can be used as good compost by this time.

【課題のiv】生ごみ処理中は大量の菌類が繁殖し膨大
な熱量を発生するが、これを合理的に且つ積極的に利用
する構造の提案は今迄無かった。高々保温を行う程度で
は積極的な利用とは言い難い。本案は内部で発生した熱
を有効利用する事を主張する。具体的に言えば、生ごみ
投入部は醗酵の進んだ部分に較べて温度が低いのは当然
であるが、通常外部加熱で補う。全体で発生する熱量と
生ごみの新規投入で必要となる熱量を較べ多少を勘案す
れば、前者が遙に多く温度も高い。よって容器壁を通じ
温度差で、又は換気排気熱の形で利用する。容器壁の温
度差は、処理物を循環させてはじめて利用可能な形に出
来る点に、特に注目すべきである。尚、補助的に加熱用
の熱源を備えることの有無は本提案の骨子に拘る要件で
は無い事を確認しておく。
Iv) During the processing of garbage, a large amount of fungi proliferate and generate an enormous amount of heat. However, there has been no proposal for a structure that uses this rationally and positively. It is hard to say that active use is enough to keep it warm at most. The present invention claims to make effective use of the heat generated inside. To put it concretely, the temperature of the garbage input section is naturally lower than that of the fermented part, but is usually supplemented by external heating. Considering the amount of heat generated as a whole and the amount of heat required for new input of garbage, the former is much more common and the temperature is high. Thus, it is used as a temperature difference through the container wall or in the form of ventilation exhaust heat. It is particularly noteworthy that the temperature difference in the vessel wall can only be brought into a usable form by circulating the treatment. It should be noted that whether or not a heat source for heating is additionally provided is not a requirement of the gist of the present proposal.

【課題のv】既に、本案の当然の帰結として生ごみが充
分実用に耐える堆肥に加工される事は説明された。要点
を踏まえれば堆肥を作るのは容易である。良い堆肥は一
種の芳香を放ち、適度の水分を保有して手にはさらさら
と心地よく、黒土に似て見た目にも効果を予感させるも
のが有る。生ごみ堆肥の終着点は此処になければならな
い。尚、本案に従えば、処理物を内部で循環させる結
果、体積が大幅に減少する事を利用して、所謂生ごみの
減容型処理が出来る事を特記しておく。減容型の場合、
言う迄も無いが、処理物が溜まれば取出さなければなら
ない。しかし、取出した処理物は堆肥であり、処分に困
ることが無いのは、他の方法に優る利点である。
Problem v: It has already been explained that garbage is processed into a sufficiently practical compost as a natural consequence of the present invention. It is easy to make compost considering the point. Good compost emits a kind of fragrance, retains a moderate amount of water, is smooth and comfortable to the hands, and has a similar appearance to black soil, which can be expected to look good. The final point of the garbage compost must be here. It should be noted that according to the present invention, the so-called garbage volume reduction type processing can be performed by utilizing the fact that the volume of the processed material is greatly reduced as a result of circulating the processed material inside. In case of reduced volume type,
Needless to say, if the processed material accumulates, it must be removed. However, it is an advantage over other methods that the removed material is compost and there is no trouble in disposal.

【留意点1】醗酵処理では使う菌類が重要である。高温
菌が望ましい。嫌気性の菌類では温度が上がらないので
水分が抜けず体積減少が極端に少ないので、使えない。
この意味で、以前流行した乳酸菌系統は、生ごみ処理に
使えない。もし強いて本発明の装置に使えば、間違いな
く発明自体の評価を誤る結果に成る。
[Note 1] The fungi used are important in the fermentation process. Thermophilic bacteria are preferred. Anaerobic fungi cannot be used because the temperature does not rise and moisture is not released and the volume decrease is extremely small.
In this sense, strains of lactic acid bacteria that were prevalent in the past cannot be used for garbage disposal. If used in the device of the present invention, it would undoubtedly result in an incorrect evaluation of the invention itself.

【留意点2】菌類選択の目易は良い堆肥が速く出来る事
で、本案は高温菌を推奨する。高温菌は可能な限り好気
的条件に置くべきで、嫌気状態では温度が上がらず、処
理速度も遅くなる。又、菌類の変態が起こり、臭気が発
生し易くなる。防止のためには温度が低下しない程度に
給気量が多く、細部まで換気するような構造にすること
が肝要である。
[Points to be noted 2] It is easy to select fungi because good compost can be made quickly. Thermophilic bacteria should be placed under aerobic conditions as much as possible. In an anaerobic condition, the temperature does not rise and the processing speed decreases. In addition, transformation of fungi occurs, and odor tends to occur. In order to prevent this, it is important to provide a structure that supplies a large amount of air to the extent that the temperature does not decrease and ventilates the details.

【留意点3】生ごみ投入部では循環した処理物と良く撹
拌する必要がある。比率は生ごみの種類、温度、菌種で
異なるから、個々に実験で確認する事が望ましい。
[Note 3] In the garbage input section, it is necessary to mix well with the circulated processed material. Since the ratio varies depending on the type of garbage, the temperature, and the type of bacteria, it is desirable to confirm the ratio individually by experiment.

【留意点4】処理物を内部に留めておけば堆肥化が進
み、やがては土壌になる。従って、本案により堆肥を製
造する場合、処理物を取り出すべく適当な時期がある事
に留意する。この点は設計上重要であり、生ごみ投入量
と全容積の比率が不適当では、良い堆肥が出来ない意味
もある。生ごみの種類(例えば剪定廃材と家庭の生ご
み)で比率を変える必要があり、設計に際し夫々実験的
に求める。醗酵部の容積には、生ごみの性質と量を変動
要素とした適正値が、勿論ある。
[Note 4] If the treated material is kept inside, composting will proceed and eventually it will become soil. Therefore, when producing compost according to the present invention, it should be noted that there is an appropriate time to take out the processed material. This point is important in the design, and if the ratio of the input amount of garbage to the total volume is inappropriate, there is also a meaning that good compost cannot be formed. It is necessary to change the ratio depending on the type of garbage (for example, pruned waste wood and household garbage), and each is determined experimentally when designing. The volume of the fermentation unit has, of course, an appropriate value in which the nature and amount of garbage are variable factors.

【留意点5】装置を使い始める時は、他所で処理中の処
理物を上段に充填して開始する。従って、初期加熱用の
熱源は原則として備える必要が無い。
[Note 5] When starting to use the apparatus, the process to be processed in another place is filled in the upper stage and started. Therefore, it is not necessary to provide a heat source for initial heating in principle.

【実施例】第1図に概略の構造例を示す。1は本体であ
る。充分な断熱材2を用い保温に留意する。3は生ごみ
投入口である。醗酵容器4・5は上下2層に別れてお
り、醗酵の進んだ発熱量の大きい方が下段を通る。各層
内部には撹拌と移送用を兼ねる撹拌軸6・7を備える。
各撹拌軸には羽根(図面では省略)が取り付けられてお
り、各インバータ用のモートル8・9で駆動する。各槽
にはコンプレッサ10から送気管11・12を通して圧
縮空気が供給される。蒸気を含む排気は排気管13・1
4を通って放熱しながら、最終的には熱交換器15に導
かれ、給気を温めた後外部に排出される。処理物は排出
口16から取り出される。
FIG. 1 shows a schematic structural example. 1 is a main body. Use enough heat insulating material 2 and keep warm. Reference numeral 3 denotes a food waste input port. The fermentation vessels 4 and 5 are divided into upper and lower layers, and the one with the larger calorific value of the fermentation passes through the lower stage. The inside of each layer is provided with stirring shafts 6 and 7 for both stirring and transfer.
Blades (omitted in the drawings) are attached to each stirring shaft, and are driven by motors 8.9 for each inverter. Compressed air is supplied to each tank from the compressor 10 through air supply pipes 11 and 12. The exhaust containing steam is the exhaust pipe 13.1
While radiating heat through 4, the air is finally led to the heat exchanger 15, where the supply air is heated and then discharged outside. The processed material is taken out from the outlet 16.

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

【図1】 実施例の生ごみ処理機構造図FIG. 1 is a structural diagram of a garbage processing machine according to an embodiment.

【符号の説明】[Explanation of symbols]

1 本体 2 断熱材 3 生ごみ投入口 4・5 醗酵容器 6・7 撹拌軸 8・9 インバータ用モートル 10 コンプレッサ 11・12 送気管 13・14 排気管 15 熱交換器 16 処理物排出口 DESCRIPTION OF SYMBOLS 1 Main body 2 Insulation material 3 Garbage input port 4.5 Fermentation container 6.7 Stirring shaft 8.9 Inverter motor 10 Compressor 11.12 Air supply pipe 13.14 Exhaust pipe 15 Heat exchanger 16 Processed material discharge port

Claims (3)

【特許請求の範囲】 以下で醗酵処理とは、焼却以外の、意図するしないに関
係無く結果的に菌類等を利用することになる場合も含
め、その処理方法を称して生ごみ等の醗酵処理方法と規
定する。
[Claims] In the following, the term "fermentation treatment" refers to a fermentation treatment of garbage and the like, including a method other than incineration and a case where fungi and the like are eventually used regardless of unintended consequences. Defined as a method.
【請求項1】 生ごみ等の醗酵処理において、醗酵処理
した物(以下処理物と称す)を処理過程で順次循環さ
せ、新規投入する生ごみ等を順次循環させた処理物に混
合する事を特徴とする。
In the fermentation treatment of garbage and the like, fermented products (hereinafter referred to as "processed products") are sequentially circulated in the process, and newly introduced garbage and the like are mixed with the circulated processed products. Features.
【請求項2】 処理物を循環させる過程で処理中の物が
発する醗酵熱を別部の処理中の物の加熱に利用する構造
を持つ事を特徴とする。
2. A structure in which the heat of fermentation generated by the material being processed in the process of circulating the processed material is used for heating the material being processed in another part.
【請求項3】 処理物を少なくとも1回以上処理装置内
で循環させる事を特徴とする。尚、同一槽内で循環させ
なくとも本案の趣旨に沿う目的であれば、本請求項の範
囲のうちである。
3. The method according to claim 1, wherein the processing object is circulated at least once in the processing apparatus. It should be noted that, if the purpose does not circulate in the same tank, but falls within the scope of the present invention, it is within the scope of the claims.
JP10377878A 1998-12-14 1998-12-14 Disposal of garbage or the like Pending JP2000176428A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10377878A JP2000176428A (en) 1998-12-14 1998-12-14 Disposal of garbage or the like

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10377878A JP2000176428A (en) 1998-12-14 1998-12-14 Disposal of garbage or the like

Publications (1)

Publication Number Publication Date
JP2000176428A true JP2000176428A (en) 2000-06-27

Family

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP10377878A Pending JP2000176428A (en) 1998-12-14 1998-12-14 Disposal of garbage or the like

Country Status (1)

Country Link
JP (1) JP2000176428A (en)

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