JPH07241542A - Method and apparatus for fermentation of organic material - Google Patents

Method and apparatus for fermentation of organic material

Info

Publication number
JPH07241542A
JPH07241542A JP6059811A JP5981194A JPH07241542A JP H07241542 A JPH07241542 A JP H07241542A JP 6059811 A JP6059811 A JP 6059811A JP 5981194 A JP5981194 A JP 5981194A JP H07241542 A JPH07241542 A JP H07241542A
Authority
JP
Japan
Prior art keywords
fermentation
organic material
temperature
air supply
fermenter
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
JP6059811A
Other languages
Japanese (ja)
Inventor
Akio Ono
秋夫 大野
Tatsuo Nagai
達夫 永井
Yukie Otsuji
幸枝 尾辻
Yuichi Yoshino
勇一 吉野
Masakazu Yokota
正和 横田
Koji Yoshimoto
耕司 吉本
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.)
Japan Steel Works Ltd
Original Assignee
Japan Steel Works 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 Japan Steel Works Ltd filed Critical Japan Steel Works Ltd
Priority to JP6059811A priority Critical patent/JPH07241542A/en
Publication of JPH07241542A publication Critical patent/JPH07241542A/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)
  • Treatment Of Sludge (AREA)
  • Fertilizers (AREA)

Abstract

PURPOSE:To uniformly and efficiently subject to an org. material to fermentation treatment. CONSTITUTION:An org. material is frequently stirred while the water content thereof is kept under air supply environment regulated in temp. to be subjected to aerobic fermentation. A fermentation treatment apparatus is constituted of a hermetically closed fermentation tank 1, the stirring device 20 installed in the fermentation tank 1, an air supply device 9b capable of regulating temp. and air quantity, a deodorizing and exhaust device 10a for the gas from the interior of the fermentation tank and a water sprinkler 12 capable of regulating temp. and a flow rate. Therefore, the org. material can be held under environment suitable for fermentation and can be subjected to uniform fermentation treatment at high speed.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、都市ごみ、家畜糞尿、
農林水産業および食品加工業廃棄物、汚泥等の有機質材
料を高速で発酵処理する発酵処理方法及び処理装置に関
するものである。
BACKGROUND OF THE INVENTION The present invention relates to municipal waste, livestock manure,
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a fermentation treatment method and treatment device for high-speed fermentation treatment of organic materials such as wastes from agriculture, forestry and fisheries and food processing industries and sludge.

【0002】[0002]

【従来の技術】従来、都市ごみ、農林水畜産および食品
加工業廃棄物等の有機廃棄物は、主として焼却処理さ
れ、埋め立てに利用されたり、最終処分場で処分された
りしている。また、家畜糞尿や一部の都市ごみ等を好気
性発酵させて堆肥化し、直接農作物に使用することも実
用化されている。ところで、前記した有機廃棄物の焼却
処理では、大量の二酸化炭素、窒素酸化物(NOx)、
硫黄酸化物(SOx)等が大気中に放出され、地球の温
暖化、酸性雨、大気汚染等を引き起こす原因となってお
り、これらは食物連鎖、さらには生物の生態系まで悪影
響を及ぼし始めている。このため有機廃棄物について
も、前記堆肥化と同様に発酵処理して減容化することが
考慮されており、この方法は埋め立てや焼却に比べて環
境に優しい処理方法といえる。いずれにしても有機質材
料である有機廃棄物を、堆肥化や減容化のために発酵処
理することは、ゴミの減量化のために有効な方法であ
る。
2. Description of the Related Art Conventionally, organic wastes such as municipal solid wastes, agricultural, forestry, water and livestock and food processing industry wastes are mainly incinerated, used for landfill, or disposed at a final disposal site. In addition, it has been put into practical use that animal manure and some municipal solid waste are aerobically fermented to be composted and directly used for agricultural products. By the way, in the above-mentioned incineration of organic waste, a large amount of carbon dioxide, nitrogen oxides (NOx),
Sulfur oxides (SOx) are released into the atmosphere, causing global warming, acid rain, air pollution, etc. These are beginning to adversely affect the food chain and even the biological ecosystem. . For this reason, it is considered that the organic waste is also subjected to fermentation treatment to reduce its volume as in the case of the above-mentioned composting, and this method can be said to be an environmentally friendly treatment method compared to landfill or incineration. In any case, fermenting organic waste, which is an organic material, for composting or volume reduction is an effective method for reducing the amount of waste.

【0003】従来から堆肥化装置としては各種の装置が
提案されており、その一つとして例えば特公昭64−1
435号公報に示されるようなスクープ式堆肥化装置が
ある。スクープ式堆肥化装置は、発酵槽内に投入される
処理材料を攪拌移送装置(スクープ式)で攪拌しつつ移
送するとともに、堆積させている処理材料に対し、パン
チングプレートからなる槽底の下部空気室から、常時通
気することによって好気性発酵をさせて堆肥化するもの
である。 また、スクープ式堆肥化装置の他に、ダノ式
やパドル式等の堆肥化装置があるが、いずれの方式も空
気を処理材料の下側から供給し、それと同時にそれぞれ
の攪拌装置で処理材料を攪拌するものである。
Various types of composting devices have been proposed in the past, and one of them has been proposed, for example, in Japanese Examined Patent Publication No. 64-1.
There is a scoop type composting device as shown in Japanese Patent No. 435. The scoop-type composting device transfers the processing material to be put into the fermentation tank while stirring it with a stirring transfer device (scoop type), and at the same time, it lowers the air below the tank consisting of a punching plate against the accumulated processing material. By constantly ventilating the room, aerobically fermenting it to compost. In addition to the scoop type composting device, there are Dano type and paddle type composting devices. In both methods, air is supplied from the lower side of the processing material, and at the same time, the processing material is supplied by each agitator. Stir it.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、上記の
ような従来の堆肥化装置では、長期間の堆肥化装置の稼
働に伴って、発酵槽の底面で処理材料や底面上敷かれる
木材チップ等の一部がこびりつき、さらにこれが積み重
なって板状に圧縮硬化したものとなる。この現象は、原
料投入部側の余分な水分がまだ十分に排出されていない
部分において特に著しく、板状化した硬化部は、処理材
料投入部側から発酵槽の長さの半分以上にわたって形成
され、水も空気も通しにくいものとなり、槽底面からの
散気を阻害して、通気の均一性を著しく損なうという欠
点がある。このため、投入した処理材料の脱水や処理材
料内への空気の吹き込みが不十分となり、嫌気性発酵の
状態になり悪臭が発生する原因となったり、堆肥化が遅
れて堆肥化装置の能力を低下させる原因となっていた。
However, in the conventional composting apparatus as described above, as the composting apparatus is operated for a long period of time, one of the treated materials and the wood chips on the bottom surface of the fermenter is The parts stick to each other, and these are piled up to be compressed and hardened into a plate shape. This phenomenon is particularly remarkable in the part where the excess water on the raw material feeding part side is not yet sufficiently discharged, and the plate-shaped hardening part is formed over the half of the length of the fermentation tank from the processing material feeding part side. However, it has the disadvantage that it becomes difficult for water and air to pass through, hinders air diffusion from the bottom of the tank, and significantly impairs the uniformity of ventilation. For this reason, dehydration of the input processing material and blowing of air into the processing material become insufficient, causing an anaerobic fermentation state and causing a bad odor, or delaying composting and increasing the capacity of the composting device. It was the cause of the decrease.

【0005】これに対し、槽底部の全面から強制的に通
気空気は送り込む方法もある。しかし、この方法では空
気は抵抗の少ない槽壁部に沿って流れやすく、壁部付近
の処理材料の方に多く流れ、槽壁部から離れた中間部の
処理材料中には少量しか流れないという現象が生じる。
したがって、処理材料中の好気性微生物の活動に必要な
空気を同槽内の堆積処理材料全体に均一に供給できない
ため、良好な好気性発酵が成されない部分が生じるとい
う欠点があった。特に、処理材料は通常は少なくとも一
定時間は堆積静置されているから、上記の現象によっ
て、通気されている空気中の酸素濃度は処理材料内部の
位置によって大きく異なり、反応速度は相当異なると考
えられる。このため定期的に「切り返し」と呼ばれる攪
拌操作を行っているが、通常の攪拌では空気濃度の均一
性を確保することが困難であり、発酵槽内部の反応状態
は極めて不均一であるといえる。この攪拌の回数を増や
したり、反応促進のために大量に通気する方法も考えら
れるが、処理材料の温度が低下してかえって反応が阻害
されるという問題がある。本発明は、このような従来の
不均一な通気を改良して極力これを均一化して、発酵槽
内の処理材料全体の良好な好気性発酵を行うことを目的
とする。
On the other hand, there is also a method in which the ventilation air is forcibly sent from the entire bottom surface of the tank. However, in this method, the air easily flows along the wall of the tank where the resistance is low, the air flows more toward the processing material near the wall, and only a small amount flows into the processing material in the middle part apart from the tank wall. The phenomenon occurs.
Therefore, since the air required for the activity of aerobic microorganisms in the treated material cannot be uniformly supplied to the entire deposited treated material in the same tank, there is a disadvantage that good aerobic fermentation is not performed in some parts. In particular, since the treatment material is usually deposited and allowed to stand for at least a certain period of time, it is considered that the oxygen concentration in the aerated air greatly differs depending on the position inside the treatment material due to the above phenomenon, and the reaction rate is considerably different. To be For this reason, a stirring operation called "cut back" is regularly performed, but it is difficult to ensure the uniformity of the air concentration by normal stirring, and it can be said that the reaction state inside the fermenter is extremely uneven. . A method of increasing the number of times of stirring or aeration with a large amount to promote the reaction can be considered, but there is a problem that the temperature of the treatment material is lowered and the reaction is rather hindered. It is an object of the present invention to improve such conventional non-uniform aeration and make it uniform as much as possible to perform good aerobic fermentation of the entire treated material in the fermenter.

【0006】[0006]

【課題を解決するための手段】堆肥化装置は、発酵槽内
に処理材料を入れ、これを発酵させて堆肥とする装置で
ある。堆肥化反応は微生物が関与する一種の発酵反応で
あり、酸化反応である。処理材料に供給される酸素を消
費して微生物が増殖し、これに併行して処理材料の分解
が進む。反応に関与する微生物は雑多なものであり、多
くの素反応を司っている。総括反応で表現すると、堆肥
化反応とは 有機質材料+酸素 = 堆肥+炭酸ガス+水+アンモニ
ア であるといえる。微生物の増殖及び生理活性には、酸素
以外にも処理材料の含水率や温度、pH等の環境要因が
大きく影響し、発酵反応の結果、これらの要因が様々な
形で影響を受ける。本発明者らはこの堆肥化の原点に立
ち戻り鋭意、研究を行った結果、堆肥化、減容化を含め
て高速での発酵処理が可能である本発明を完成させた。
[Means for Solving the Problems] A composting device is a device for putting a treatment material in a fermenter and fermenting the processed material to form a compost. The composting reaction is a kind of fermentation reaction involving microorganisms and is an oxidation reaction. Oxygen supplied to the processing material is consumed and microorganisms grow, and in parallel with this, decomposition of the processing material proceeds. Microorganisms involved in the reaction are diverse and control many elementary reactions. Expressed as a general reaction, it can be said that the composting reaction is organic material + oxygen = compost + carbon dioxide gas + water + ammonia. In addition to oxygen, environmental factors such as water content, temperature, and pH of the treatment material greatly affect the growth and physiological activity of microorganisms, and as a result of the fermentation reaction, these factors are affected in various ways. The present inventors have returned to the origin of this composting, and as a result of diligent research, have completed the present invention capable of high-speed fermentation treatment including composting and volume reduction.

【0007】すなわち、本発明の有機質材料の発酵処理
方法は、温度調節された給気環境下で、有機質材料の含
水率を適正範囲に維持しつつ、有機質材料を頻繁に攪拌
して好気性発酵させることを特徴とする。
That is, according to the method for fermenting an organic material of the present invention, the aerobic fermentation is performed by frequently stirring the organic material while maintaining the water content of the organic material in an appropriate range under a temperature-controlled air supply environment. It is characterized by

【0008】さらに、給気環境の温度調節は、第2の発
明に示すように温度を調節した加熱空気の給気によって
行うことができ、また、第3の発明に示すように、有機
質材料が収容されている発酵槽を加熱することによって
行うことも可能である。これらは単独で行うことは勿論
のこと、組み合わせて行うことも可能である。 そし
て、この給気環境の温度は、第4の発明に示すように、
35〜80℃に調節するのが望ましい。なお、給気は、
従来と同様に発酵槽の底面から行うことも可能であり、
また、雰囲気中に直接送風する構成であってもよい。雰
囲気中に直接送風する場合には、単独で行う他に、底面
からの散気、給気と組み合わせることも可能である。ま
た、有機質処理材料の適正範囲の含水率としては、第5
の発明でいうように、30〜60%が望ましい。含水率
の維持は、有機質材料に散水(噴霧が望ましい)するこ
とによって達成されるが、この他にまたは散水と組み合
わせて、加湿した給気によって行うことも可能である。
Further, the temperature of the air supply environment can be adjusted by supplying heated air whose temperature is adjusted as shown in the second aspect of the invention, and as shown in the third aspect of the invention, the organic material is It is also possible to do this by heating the contained fermenter. These may be performed alone or in combination. The temperature of the air supply environment is, as shown in the fourth invention,
It is desirable to adjust the temperature to 35 to 80 ° C. The air supply is
It is also possible to perform from the bottom of the fermenter as in the past,
Alternatively, the air may be blown directly into the atmosphere. When the air is blown directly into the atmosphere, it is possible to combine it with air diffusion or air supply from the bottom, in addition to performing it alone. The water content in the proper range of the organic treatment material is the fifth
As stated in the above invention, 30 to 60% is desirable. Maintaining the water content is achieved by sprinkling (preferably spraying) the organic material, but it can also be done by a humidified air supply in addition to or in combination with sprinkling.

【0009】さらに、本発明の発酵処理装置は、密閉型
発酵槽と、該発酵槽内に設けられた攪拌装置と、前記発
酵槽内に給気する温度及び風量の調節装置を具備した給
気装置と、前記発酵槽内から排気する脱臭装置を具備し
た排気装置と、前記発酵槽内に散水する温度及び流量の
調節装置を具備した散水装置とを有することを特徴とす
る。なお、密閉型の発酵槽は、保温性が良好であるのが
望ましく、保温性のよい材料で構成したり、断熱材を張
り付けたりするのが望ましい。上記攪拌装置としては、
スクープ式攪拌装置を例示することができるが、これに
限定されるものではなく、パドル式、ドラム式、ロータ
リーキルン式等すべてのものを利用できる。また、給気
装置は、発酵槽の底面に配管接続することができ、その
他に、発酵槽の空間に直接送風するように設けることも
できる。この場合に、発酵槽の底面に散気装置や、給気
装置を合わせて接続することも可能であり、さらに底面
の給気装置に、温度及び風量の調節装置を具備させるこ
とも可能である。また、散水装置としては、水を噴霧す
るものが望ましい。
Further, the fermentation treatment apparatus of the present invention comprises a closed type fermenter, an agitator provided in the fermenter, and an air supply device for adjusting the temperature and air volume of the air supplied to the fermenter. The apparatus is characterized by having an apparatus, an exhaust apparatus equipped with a deodorizing apparatus for exhausting gas from the inside of the fermentation tank, and a water sprinkling apparatus equipped with an apparatus for adjusting the temperature and flow rate of water sprayed into the fermentation tank. The closed type fermenter preferably has a good heat retaining property, and is preferably made of a material having a good heat retaining property or attached with a heat insulating material. As the stirring device,
Although a scoop type stirring device can be exemplified, the scoop type stirring device is not limited to this, and any paddle type, drum type, rotary kiln type or the like can be used. Further, the air supply device can be connected to the bottom surface of the fermenter by piping, and in addition, the air supply device can be provided so as to directly blow air into the space of the fermenter. In this case, it is possible to connect an air diffuser or an air supply device to the bottom surface of the fermenter together, and it is also possible to equip the bottom air supply device with a device for adjusting the temperature and the air volume. . As the sprinkler, it is desirable to spray water.

【0010】[0010]

【作用】すなわち、本発明の発酵処理方法によれば、有
機質材料を頻繁に攪拌しながら給気することによって、
有機質材料と空気との接触が効率よくなされる。さら
に、有機質材料は温度調整された給気環境におかれてい
るので、有機質材料の温度低下が防止されて適切な温度
におかれ、さらに含水率が適正範囲に維持されているの
で、発酵反応速度を最大に維持したまま発酵を進めるこ
とができ、高速で発酵処理することができる。
In other words, according to the fermentation treatment method of the present invention, by frequently agitating the organic material,
The contact between the organic material and air is made efficiently. Furthermore, since the organic material is placed in a temperature-controlled air supply environment, the temperature drop of the organic material is prevented, the organic material is kept at an appropriate temperature, and the water content is maintained in an appropriate range. Fermentation can be carried out while maintaining the maximum speed, and fermentation processing can be performed at high speed.

【0011】さらに、本発明の発酵処理装置によれば、
発酵槽内に適切な温度と風量で給気することができる。
しかも発酵槽は密閉構造であるので、発酵槽は、所望の
温度に安定的に保持され、また季節や天候による変動の
影響を小さくできる。そして、散水装置によって流量を
調整しつつ散水を行うことができるので、有機質材料を
適切な含水率に容易に維持することができる。また、散
水は温度の調節が可能であり、散水によって有機質材料
の温度が変動して発酵に悪影響がでることを防止でき
る。
Further, according to the fermentation treatment apparatus of the present invention,
It is possible to supply air to the fermenter at an appropriate temperature and air volume.
Moreover, since the fermenter has a closed structure, the fermenter can be stably maintained at a desired temperature and the influence of fluctuations due to seasons and weather can be reduced. Then, since the water can be sprinkled while adjusting the flow rate by the sprinkler, the organic material can be easily maintained at an appropriate water content. In addition, the temperature of the water sprinkling can be controlled, and it is possible to prevent the temperature of the organic material from fluctuating and adversely affecting the fermentation.

【0012】なお、本発明は高速で堆肥化、減容化する
だけにとどまらない。高速発酵と同様に世の中の強い要
求として無臭気発酵がある。発酵時の臭気の発生は処理
材料の温度が60℃以上で著しくなるから、これよりも
低温で発酵させる必要がある。本発明では発酵環境を制
御できるので、低臭気発酵が可能である。また、通気を
行いかつ攪拌を行う操作は発酵処理の中の一次発酵と呼
ばれるものであり、通常その後室温で同程度の期間放置
して、いわゆる熟成処理を行う。これが二次発酵と呼ば
れる過程で、一次発酵で残された難分解性の有機質物を
時間をかけて発酵させる。よって、本発明で発酵させた
材料をさらに二次発酵させることも可能である。
The present invention is not limited to high speed composting and volume reduction. Odorless fermentation is one of the strongest demands in the world as well as high-speed fermentation. The generation of odor during fermentation becomes remarkable when the temperature of the treated material is 60 ° C. or higher, and thus it is necessary to ferment at a temperature lower than this. Since the fermentation environment can be controlled in the present invention, low odor fermentation is possible. The operation of aeration and agitation is called primary fermentation in the fermentation process, and it is usually left to stand at room temperature for a similar period of time to perform a so-called aging process. In the process called secondary fermentation, the hardly decomposable organic matter remaining in the primary fermentation is fermented over time. Therefore, the material fermented in the present invention can be further secondarily fermented.

【0013】次に、発酵条件等についてより具体的に説
明する。 (1)給気環境を35〜80℃に温度調節することによ
り最も効率よく発酵が進行する。そして、発酵の反応率
が80%までは処理材料の温度を35〜80℃、好適に
は45〜70℃に維持することで発酵反応速度を最大に
維持したまま発酵反応を進めることができる。 (2)処理材料の含水率を30〜60%に維持するの
は、上記温度の調節と同様に発酵を良好に進行させるた
めである。好適には、発酵の反応率が80%までは処理
材料の含水率を30〜60%、好適には50〜60%に
維持し、その後徐々に減少して反応終了時には処理材料
の含水率を30〜50%に維持することが望ましい。 (3)攪拌は、10分間〜12時間の間隔で攪拌するこ
とにより、有機質材料を空気と効率よく接触させること
ができる。12時間を越える間隔では、その作用が十分
ではなく、10分未満の間隔で攪拌しても、効果が飽和
するだけでなく、作業が面倒になるので、上記範囲が望
ましい。 (4)さらに、本発明の有機質材料は前処理によって好
適には、平均粒径または平均長さで1〜20mmに粉砕
することが望ましい。また、有機質材料の処理開始時の
含水率を55〜70%とするのが望ましい。
Next, the fermentation conditions and the like will be described more specifically. (1) Fermentation proceeds most efficiently by controlling the temperature of the air supply environment to 35 to 80 ° C. Then, by maintaining the temperature of the treated material at 35 to 80 ° C., preferably 45 to 70 ° C. until the reaction rate of fermentation is 80%, the fermentation reaction can be carried out while maintaining the fermentation reaction rate at the maximum. (2) The reason why the water content of the treated material is maintained at 30 to 60% is to allow the fermentation to proceed satisfactorily as in the case of adjusting the temperature. Suitably, the water content of the treated material is maintained at 30 to 60%, preferably 50 to 60% until the reaction rate of fermentation is 80%, and then gradually decreased to reduce the water content of the treated material at the end of the reaction. It is desirable to maintain 30 to 50%. (3) The stirring can efficiently bring the organic material into contact with air by stirring at intervals of 10 minutes to 12 hours. If the interval exceeds 12 hours, the action is not sufficient, and even if the mixture is stirred for less than 10 minutes, the effect is saturated and the work becomes troublesome. Therefore, the above range is preferable. (4) Furthermore, it is preferable that the organic material of the present invention is preferably pulverized by pretreatment so as to have an average particle size or average length of 1 to 20 mm. Further, it is desirable that the water content of the organic material at the start of treatment is 55 to 70%.

【0014】[0014]

【実施例】先ず、本発明の発酵処理装置を図1に基づい
て説明する。水平直線状で溝型の発酵槽1が水平に設置
され、この発酵槽1の側壁上に、スクープ装置20aを
吊り下げたスクープ式切り返し装置20が配置されてお
り、スクープ式切り返し装置20は、図示しない駆動装
置で発酵槽1の長尺方向に往復動するように構成されて
いる。また、スクープ装置20aは、傾斜方向およびス
クープの回転方向を切り替えできるように構成されてい
る。さらに該発酵槽1の周囲には発酵槽1全体を覆うよ
うに、両側壁と天板と底板からなるカバー2が配置され
ており、発酵槽1は密閉型になっている。上記カバー2
の後端(図1左方)上部には、コンベヤー3で運ばれる
有機質材料4を投入する投入口5が設けられており、一
方、カバー2の前端側(図1右方)底部には処理済みの
有機質材料を排出する排出口6が形成されており、排出
口6の下方には排出スクリュウフィーダ7が設置されて
いる。
EXAMPLE First, the fermentation treatment apparatus of the present invention will be described with reference to FIG. The horizontal linear groove type fermenter 1 is installed horizontally, and on the side wall of the fermenter 1, a scoop-type turning device 20 in which a scoop device 20a is hung is arranged, and the scoop-type turning device 20 is It is configured to reciprocate in the lengthwise direction of the fermenter 1 by a drive device (not shown). Further, the scoop device 20a is configured so that the inclination direction and the rotation direction of the scoop can be switched. Further, a cover 2 composed of both side walls, a top plate and a bottom plate is arranged around the fermentation tank 1 so as to cover the entire fermentation tank 1, and the fermentation tank 1 is of a hermetic type. The cover 2
A charging port 5 for charging the organic material 4 carried by the conveyor 3 is provided at the upper part of the rear end (left side of FIG. 1), while the processing part is provided at the bottom part of the front end side (right side of FIG. 1) of the cover 2. A discharge port 6 for discharging the used organic material is formed, and a discharge screw feeder 7 is installed below the discharge port 6.

【0015】また、カバー2には、後端側側壁に給気口
9、前端側天板に排気口10が形成されており、給気口
9には、バルブ9aを介して、温度および風量の調節が
可能な給気装置9bが接続されている。一方、排気口1
0には、脱臭・排気装置10aが接続されている。さら
に、カバー2の天板には、複数の噴霧ノズル11が下方
に噴霧するように取り付けられており、各噴霧ノズル1
1…11は、配管およびバルブ12a…12a、12b
を介して、温度及び流量の調整が可能な噴霧装置12に
接続されて散水装置が構成されている。また、発酵槽1
の底部は、多孔板で構成され、その下に空気室13が設
けられており、この空気室13は、バルブ13aを介し
て通気装置13bに連結されている。なお、図示はしな
いが、発酵槽1の底部から、水を抜くことも可能であ
り、この排出水(汚水)を前記噴霧装置12で使用する
ことも可能である。
The cover 2 has an air supply port 9 formed on the rear side wall and an exhaust port 10 formed on the front end side top plate. The air supply port 9 is provided with a temperature and an air volume through a valve 9a. An air supply device 9b capable of adjusting is connected. On the other hand, exhaust port 1
A deodorization / exhaust device 10a is connected to 0. Further, a plurality of spray nozzles 11 are attached to the top plate of the cover 2 so as to spray downward, and each spray nozzle 1
1 ... 11 are piping and valves 12a ... 12a, 12b
The spraying device is configured by being connected to the spraying device 12 capable of adjusting the temperature and the flow rate via. Also, fermenter 1
The bottom part of is formed of a perforated plate, and an air chamber 13 is provided below it, and this air chamber 13 is connected to a ventilation device 13b via a valve 13a. Although not shown, it is also possible to drain water from the bottom of the fermenter 1, and this discharged water (dirty water) can be used in the spraying device 12.

【0016】次に、上記装置の動作に従って本発明の処
理法方法を説明する。水分、粒度などの調整がなされた
有機質材料4を、コンベヤー3によって投入口5から発
酵槽1内に搬入する。発酵槽1内には、温度を調節した
加熱空気が給気装置9bから給気口9を通して、所定の
風量で連続又は間欠的に給気されており、発酵槽1内の
温度が所定範囲内(35〜80℃)に保持されている。
また、これと合わせて通気装置13bを作動させ、空気
室13を通して発酵槽1の底部に通気することもでき
る。さらに、発酵槽1内の温度が十分に高い場合や、温
度を低下させたい場合には、給気装置9bを停止して、
通気装置13bのみを作動させることもできる。
Next, the processing method of the present invention will be described according to the operation of the above apparatus. The organic material 4 whose water content and particle size have been adjusted is carried into the fermenter 1 from the charging port 5 by the conveyor 3. In the fermentation tank 1, heated air whose temperature is adjusted is continuously or intermittently supplied from the air supply device 9b through the air supply port 9 at a predetermined air volume, and the temperature in the fermentation tank 1 is within a predetermined range. It is maintained at (35 to 80 ° C).
Further, in conjunction with this, the ventilation device 13b can be operated to ventilate the bottom of the fermenter 1 through the air chamber 13. Furthermore, when the temperature in the fermenter 1 is sufficiently high or when it is desired to lower the temperature, the air supply device 9b is stopped,
It is also possible to operate only the ventilation device 13b.

【0017】発酵槽1内に投入された前記有機質材料4
に対しては、スクープ式切り返し装置20を移動させな
がら、傾斜したスクープ装置20aで攪拌、移送する。
この攪拌に際しては、スクープ装置20aの傾斜方向お
よびスクープの回転方向を適宜切り替えることによっ
て、有機質材料4の移動を抑制して1日に10〜15回
の回数で頻繁に攪拌を行うことが可能である。また発酵
槽1内の有機質材料4の含水率を、異なる位置毎(長手
方向に対し)に適宜調べ、その結果に基づいて各噴霧ノ
ズル11…11のバルブ12a…12aをそれぞれ調整
して、各位置毎の有機質材料4の含水率が30〜60%
になるように調整する。なお、散水で使用する水は、噴
霧装置12で60℃に加熱されている。 また、発酵処
理中には発酵槽1内はほぼ密閉されており、内部の空気
は、排気口10から吸引されて脱臭・排気装置10aで
処理がなされるので、装置の周囲への悪臭の漏洩が確実
に防止されている。上記した動作を繰り返して、発酵槽
内で20日を経過した有機質材料を排出口6から排出す
る。得られた処理済材料は二次発酵(発酵進行度80%
以上)にまで進行している。同日数の処理を行う従来例
では、一次発酵(約40%)させる程度であり、本発明
の処理済材料は、従来材に比べて2倍またはそれ以上で
発酵が進行している。また、本発明では材料全体で均一
に発酵が進行している。
The organic material 4 charged in the fermenter 1
In contrast, while moving the scoop type turning device 20, the inclined scoop device 20a is agitated and transferred.
During this stirring, the inclination of the scoop device 20a and the rotating direction of the scoop are appropriately switched, whereby the movement of the organic material 4 can be suppressed and the stirring can be frequently performed 10 to 15 times a day. is there. Further, the water content of the organic material 4 in the fermenter 1 is appropriately examined at different positions (with respect to the longitudinal direction), and the valves 12a ... 12a of the spray nozzles 11 ... 11 are adjusted based on the results, respectively. Water content of organic material 4 at each position is 30 to 60%
Adjust so that The water used for sprinkling is heated to 60 ° C. by the spray device 12. Further, during the fermentation process, the inside of the fermenter 1 is almost sealed, and the air inside is sucked from the exhaust port 10 and processed by the deodorizing / exhausting device 10a, so that the odor leaks to the surroundings of the device. Is reliably prevented. By repeating the above-mentioned operation, the organic material which has been stored for 20 days in the fermenter is discharged from the discharge port 6. The resulting treated material is secondary fermented (fermentation progress 80%
Above). In the conventional example in which the treatment is performed for the same number of days, the primary fermentation is performed (about 40%), and the treated material of the present invention undergoes fermentation twice or more as compared with the conventional material. Further, in the present invention, fermentation is progressing uniformly throughout the material.

【0018】次に、本発明の効果を確認するため、従来
例と比較する試験を行った。表1に示す厨芥物、都市ご
み、牛糞尿及び豚糞を有機質原料として、前記実施例の
装置を用いた本発明法と、従来のスクープ式発酵装置を
用いた従来法でそれぞれ発酵処理を行い、20日経過し
た後の発酵の進行程度を比較検討した。なお、発酵の進
行程度は、発酵による処理材の減量を目安にし、減量が
ほぼ停止した時点で発酵の進行を100%とする判断方
法によって行った。重量変化では水分量の変化は除外す
る。上記試験結果を表1に示す。本発明法で処理した有
機質材料は、比較法のものに比べて、発酵進行が進んで
おり、発酵効率が向上していることが確認された。ま
た、本発明法による有機質材料は、ほぼ均質に発酵が進
行していたが、比較法のものはばらつきが大きかった。
Next, in order to confirm the effect of the present invention, a test for comparison with the conventional example was conducted. Fermentation treatment was carried out by using the kitchen waste, municipal solid waste, cattle manure and pig manure shown in Table 1 as organic raw materials according to the method of the present invention using the apparatus of the above-mentioned example and the conventional method using the conventional scoop type fermenter. The progress of fermentation after 20 days was compared and examined. The degree of progress of fermentation was determined by a method of determining the amount of the treated material by fermentation as a standard, and determining that the progress of fermentation was 100% when the reduction was almost stopped. Weight changes exclude changes in water content. The test results are shown in Table 1. It was confirmed that the organic material treated by the method of the present invention has progressed in fermentation and improved fermentation efficiency as compared with that of the comparative method. In addition, the organic material produced by the method of the present invention was fermented substantially uniformly, but the organic material produced by the comparative method had large variations.

【0019】[0019]

【表1】 [Table 1]

【0020】[0020]

【発明の効果】以上説明したように、本発明の発酵処理
方法および装置によれば、有機質材料を、均一にかつ最
適な環境下において、発酵反応速度を最大に維持したま
まで反応を進めることができるため、高速で堆肥化や減
容化を行うことができる。
As described above, according to the fermentation processing method and apparatus of the present invention, the organic material is allowed to proceed with the reaction in a uniform and optimal environment while maintaining the maximum fermentation reaction rate. Therefore, composting and volume reduction can be performed at high speed.

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

【図1】図1は本発明の一実施例の模式正面図である。FIG. 1 is a schematic front view of an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 発酵槽 2 カバー 4 有機質材料 5 投入口 6 排出口 9 給気口 10 排気口 9b 給気
装置 10a 脱臭・排気装置 11 噴霧
ノズル 12 噴霧装置 20 スク
ープ式切り返し装置 20a スクープ装置
1 Fermenter 2 Cover 4 Organic material 5 Input port 6 Discharge port 9 Air supply port 10 Exhaust port 9b Air supply device 10a Deodorization / exhaust device 11 Spray nozzle 12 Spray device 20 Scoop type turning device 20a Scoop device

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C05F 7/00 9/02 H 7537−4H (72)発明者 吉野 勇一 千葉県四街道市鷹の台1丁目3番 株式会 社日本製鋼所内 (72)発明者 横田 正和 広島県広島市安芸区船越南1丁目6番1号 株式会社日本製鋼所内 (72)発明者 吉本 耕司 広島県広島市安芸区船越南1丁目6番1号 株式会社日本製鋼所内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification number Reference number within the agency FI Technical display location C05F 7/00 9/02 H 7537-4H (72) Inventor Yuichi Yoshino 1-chome, Takanodai, Yotsukaido-shi, Chiba No. 3 Stock Company Japan Steel Works (72) Inventor Masakazu Yokota 1-1-6 Funakoshi Minami, Aki-ku, Hiroshima City, Hiroshima Prefecture Hiroshima Steel Works (72) Inventor Koji Yoshimoto 1 Funakoshi-minami, Aki-ku, Hiroshima City, Hiroshima Prefecture 6th-1st Japan Steel Works, Ltd.

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 温度調節された給気環境下で、有機質材
料の含水率を適正範囲に維持しつつ、有機質材料を頻繁
に攪拌して好気性発酵させることを特徴とする有機質材
料の発酵処理方法
1. A fermentation treatment of an organic material, which is characterized by frequently agitating the organic material to aerobically ferment it while maintaining the water content of the organic material in an appropriate range in a temperature-controlled air supply environment. Method
【請求項2】 給気環境の温度調節は、温度を調節した
加熱空気の給気によって行うことを特徴とする請求項1
記載の有機質材料の発酵処理方法
2. The temperature control of the air supply environment is performed by air supply of heated air whose temperature is adjusted.
Fermentation treatment method of the described organic material
【請求項3】 給気環境の温度調節は、有機質材料が収
容されている発酵槽を加熱することによって行うことを
特徴とする請求項1または2記載の有機質材料の発酵処
理方法
3. The method for fermenting an organic material according to claim 1, wherein the temperature of the air supply environment is adjusted by heating a fermenter containing the organic material.
【請求項4】 給気環境の温度を35〜80℃に調節す
ることを特徴とする請求項1〜3のいずれかに記載の有
機質材料の発酵処理方法
4. The method for fermenting an organic material according to claim 1, wherein the temperature of the air supply environment is adjusted to 35 to 80 ° C.
【請求項5】 有機質材料の含水率が30〜60%に維
持されていることを特徴とする請求項1〜4のいずれか
に記載の有機質材料の発酵処理方法
5. The method for fermenting an organic material according to claim 1, wherein the water content of the organic material is maintained at 30 to 60%.
【請求項6】 密閉型発酵槽と、該発酵槽内に設けられ
た攪拌装置と、前記発酵槽内に給気する温度及び風量の
調節装置を具備した給気装置と、前記発酵槽内から排気
する脱臭装置を具備した排気装置と、前記発酵槽内に散
水する温度及び流量の調節装置を具備した散水装置とを
有することを特徴とする発酵処理装置
6. A hermetically sealed fermenter, an agitator provided in the fermenter, an air supply device equipped with a device for adjusting the temperature and the amount of air supplied to the fermenter, and from the inside of the fermenter. A fermentation treatment apparatus comprising: an exhaust device equipped with a deodorizing device for exhausting gas, and a water sprinkling device equipped with a device for adjusting the temperature and flow rate of water sprayed in the fermentation tank.
JP6059811A 1994-03-07 1994-03-07 Method and apparatus for fermentation of organic material Pending JPH07241542A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6059811A JPH07241542A (en) 1994-03-07 1994-03-07 Method and apparatus for fermentation of organic material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6059811A JPH07241542A (en) 1994-03-07 1994-03-07 Method and apparatus for fermentation of organic material

Publications (1)

Publication Number Publication Date
JPH07241542A true JPH07241542A (en) 1995-09-19

Family

ID=13124000

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6059811A Pending JPH07241542A (en) 1994-03-07 1994-03-07 Method and apparatus for fermentation of organic material

Country Status (1)

Country Link
JP (1) JPH07241542A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1999030846A1 (en) * 1997-12-16 1999-06-24 Isami Fukunaga Method and system for treating organic waste
JP2003505323A (en) * 1999-07-20 2003-02-12 オーガニック・リソース・テクノロジーズ・リミテッド Organic waste treatment method
JP2007268493A (en) * 2006-03-31 2007-10-18 Seigu:Kk Fermentation method and apparatus
KR101930218B1 (en) * 2018-07-12 2019-03-14 최석봉 Odor removal and fermentation system of piggery using peatmoss and humic substances

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1999030846A1 (en) * 1997-12-16 1999-06-24 Isami Fukunaga Method and system for treating organic waste
JP2003505323A (en) * 1999-07-20 2003-02-12 オーガニック・リソース・テクノロジーズ・リミテッド Organic waste treatment method
JP2007268493A (en) * 2006-03-31 2007-10-18 Seigu:Kk Fermentation method and apparatus
KR101930218B1 (en) * 2018-07-12 2019-03-14 최석봉 Odor removal and fermentation system of piggery using peatmoss and humic substances

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