JPH11335192A - Composting of solid waste from biomass and equipment for that purpose - Google Patents

Composting of solid waste from biomass and equipment for that purpose

Info

Publication number
JPH11335192A
JPH11335192A JP10142399A JP14239998A JPH11335192A JP H11335192 A JPH11335192 A JP H11335192A JP 10142399 A JP10142399 A JP 10142399A JP 14239998 A JP14239998 A JP 14239998A JP H11335192 A JPH11335192 A JP H11335192A
Authority
JP
Japan
Prior art keywords
oxygen
floor
air
gas
solid waste
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10142399A
Other languages
Japanese (ja)
Inventor
Masahiko Ishida
昌彦 石田
Takeshi Takemoto
剛 武本
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.)
YUKISHITSU HIRYO SEIBUTSU KASS
YUKISHITSU HIRYO SEIBUTSU KASSEI RIYO GIJUTSU KENKYU KUMIAI
Original Assignee
YUKISHITSU HIRYO SEIBUTSU KASS
YUKISHITSU HIRYO SEIBUTSU KASSEI RIYO GIJUTSU KENKYU KUMIAI
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 YUKISHITSU HIRYO SEIBUTSU KASS, YUKISHITSU HIRYO SEIBUTSU KASSEI RIYO GIJUTSU KENKYU KUMIAI filed Critical YUKISHITSU HIRYO SEIBUTSU KASS
Priority to JP10142399A priority Critical patent/JPH11335192A/en
Publication of JPH11335192A publication Critical patent/JPH11335192A/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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Abstract

PROBLEM TO BE SOLVED: To supply air at a low pressure loss and to efficiently dry compost at a low pressure loss after fermentation, by the aerobic fermentation of wet bulk materials or wet coarse particles of solid biomass waste in a fermentor equipped with charging means and exhausting means for oxygen-containing pressurized gas between the bottom bed face and the upper bed face while conducting charging and exhausting gas. SOLUTION: Bulk materials or coarse particles are filled into a fermentor 1 in a state that >=0.01 wt.% ripe compost as seed bacteria is added to solid biomass waste and moisture adjustment of bulk materials, etc., is conducted, and then oxygen-containing gas (e.g. air) is supplied in a state of partial charging into a gas inlet 5 of bottom bed face and a gas inlet 52 of intermediate bed position through a gas-supply pipe 8. The oxygen-containing gas passes through the bed 2 while contacting with the bulk materials, etc., and is exhausted from the fermentor 1 through a gas exit 111 of intermediate bed position and a gas-exhaust pipe 10 above upper bed face in a reduced oxygen content. The oxygen content of exhaust gas is detected by a concentration sensor 12 for exhaust gas and the signal of the sensor 12 is transmitted to an oxygen concentration regulator 13, followed by changing air quantity supplied through a control valve 9 for air charging quantity. Treated bed is discharged as a compost product from a blowdown outlet 4 of the bottom of the fermentor.

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、生物性有機固形廃
棄物のコンポスト化方法並びにその装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for composting biological organic solid waste.

【0002】[0002]

【従来の技術】都市ごみ、家畜糞、下水汚泥等の生物性
有機固形廃棄物、アルカリ性脱水汚泥ケーキを対象と
し、各原料を槽内に構造物のないサイロ上の発酵槽に、
原料廃棄物を単純に連続した床を構成するように充填
し、槽底からのみ空気を供給して上記床を通過した空気
を、充填床上面から排気するコンポスト化方法が、特開
昭54−101769号公報、特開昭55−12199
0号公報に記載されている。
2. Description of the Related Art For bio-organic solid waste such as municipal solid waste, livestock dung, sewage sludge, and alkaline dewatered sludge cake, each raw material is fed into a fermenter on a silo with no structure in the tank.
Japanese Patent Application Laid-Open No. Sho 54-54 discloses a method in which raw material waste is simply filled to form a continuous bed, air is supplied only from the bottom of the tank, and air passing through the bed is exhausted from the top of the packed bed. No. 101768, JP-A-55-12199
No. 0 publication.

【0003】上記従来のサイロ充填方式のコンポスト化
方法は、槽内に床を高率で充填でき、槽容積を有効に使
える利点がある。しかし、設置面積を小さくしようとし
て充填床の高さを増加すると、床の底部で酸素が消費さ
れてしまい、床の中間部および上部で酸素が不足するの
みならず、圧力損失が増加して給気が困難になる恐れが
ある。
[0003] The conventional silo-filling composting method has the advantage that the tank can be filled with the floor at a high rate and the tank volume can be used effectively. However, if the height of the packed bed is increased in order to reduce the installation area, oxygen is consumed at the bottom of the bed, and not only is the oxygen deficient in the middle and upper portions of the bed, but also the pressure loss increases and the supply is increased. You may have difficulty.

【0004】[0004]

【発明が解決しようとする課題】本発明者は前記課題を
解決すべく研究を重ねた結果、以下の現象を見い出し
た。
As a result of repeated studies to solve the above problems, the present inventors have found the following phenomena.

【0005】(1) 給気を床底のみならず床底と床上
面との中間の高度からも分割して給気した。しかし、こ
の方法では給気口の極く近傍の床部分に限り酸素の欠乏
が改善されるだけで、床底のみから給気する従来方式と
同様に、床中間部および床上部で酸素が欠乏することを
見い出した。
(1) The air supply is divided not only from the floor bottom but also from an intermediate height between the floor bottom and the floor upper surface. However, in this method, oxygen deficiency is improved only in the floor part very close to the air supply port, and oxygen depletion occurs in the middle and upper parts of the floor as in the conventional method in which air is supplied only from the floor bottom. I found something to do.

【0006】その原因は、床中間部で給気を追加して
も、床底で酸素が消費され酸素の欠乏した気流で希釈さ
れるためである。さらに、圧力損失についても床底のみ
からの給気に比べれば改善されるが、依然として高いこ
とが分かった。
The reason is that even if air supply is added in the middle of the bed, oxygen is consumed at the bottom of the bed and diluted with an oxygen-deficient airflow. Further, it was found that the pressure loss was improved as compared with the air supply from only the floor bottom, but was still high.

【0007】(2) そこで、分割して給気する一方
で、個々の給気位置よりやや下方に設けた排気口から部
分的な排気を試みた。
(2) Therefore, while air is divided and supplied, partial exhaust is attempted from an exhaust port provided slightly below each air supply position.

【0008】その結果、床の厚さを適正にすれば、真上
の給気口から下方への給気が給気口の真下の排気口へ逆
流を抑制して、実質的に酸素の欠乏した排気を吸引せず
に自然に排出できることを見出した。
[0008] As a result, when the thickness of the floor is made appropriate, the supply of air downward from the air supply port directly above the air supply port suppresses the backflow to the exhaust port immediately below the air supply port, thereby substantially depleting oxygen. It has been found that the exhaust gas can be naturally discharged without suction.

【0009】本発明の目的は上記に鑑み、充填した連続
床における発酵に際して、低い圧力損失で給気して床の
酸素消費に対応でき、さらに発酵終了後、必要に応じて
行う通気乾燥に際して、圧力損失を低く維持し、かつ、
効率良く乾燥できる生物性有機固形廃棄物のコンポスト
化方法並びにその装置を提供することにある。
In view of the above, it is an object of the present invention to supply oxygen at a low pressure loss during fermentation in a packed continuous bed and to cope with oxygen consumption of the bed. Keep the pressure loss low, and
An object of the present invention is to provide a method and an apparatus for composting biological organic solid waste that can be dried efficiently.

【0010】[0010]

【課題を解決するための手段】前記目的を達成する本発
明の要旨は次のとおりである。
The gist of the present invention to achieve the above object is as follows.

【0011】〔1〕 生物性有機固形廃棄物の含湿粉粒
体もしくは含湿粗粒体を、縦方向に連続的に充填した床
に酸素含有気体を給気して好気発酵する生物性有機固形
廃棄物のコンポスト化方法において、発酵槽の床底面と
床上面との間に加圧した酸素含有気体を給気する給気手
段と、吸引せずに排気する排気手段を設けたことを特徴
とする生物性有機固形廃棄物のコンポスト化方法にあ
る。
[1] Biological properties in which aerobic fermentation is performed by feeding an oxygen-containing gas to a bed, which is continuously filled in the longitudinal direction with wet powdered granules or wet coarse granules of biological organic solid waste. In the method for composting organic solid waste, an air supply means for supplying pressurized oxygen-containing gas between a bottom surface and a top surface of a fermentation tank, and an exhaust means for exhausting without suction are provided. A feature of the present invention is a method for composting a biological organic solid waste.

【0012】〔2〕 生物性有機固形廃棄物の含湿粉粒
体もしくは含湿粗粒体を、縦方向に連続的に充填した床
に酸素含有気体を給気して好気発酵する生物性有機固形
廃棄物のコンポスト化方法において、発酵槽の床底面と
床上面との間に設けた加圧した酸素含有気体を給気する
給気手段と、吸引せずに排気する排気手段からも給排気
することにより好気発酵させ、発酵処理後、湿度不飽和
の気体を発酵時と同様に給排気して床を乾燥することを
特徴とする生物性有機固形廃棄物のコンポスト化方法に
ある。
[2] Biological properties of aerobic fermentation by feeding an oxygen-containing gas to a bed in which moisture-containing powdery granules or moisture-containing coarse particles of biological organic solid waste are continuously filled in the longitudinal direction. In the method for composting organic solid waste, a supply means for supplying pressurized oxygen-containing gas provided between the bottom surface and the top surface of the fermenter and a discharge means for discharging without suction are also provided. An aerobic fermentation process is performed by exhausting air, and after fermentation, a humidity-unsaturated gas is supplied and exhausted in the same manner as during fermentation to dry the floor, and the method for composting a biological organic solid waste is characterized in that the method is as follows.

【0013】〔3〕 生物性有機固形廃棄物の含湿粉粒
体もしくは含湿粗粒体を、縦方向に連続的に充填した床
に酸素含有気体を給気して好気発酵させる生物性有機固
形廃棄物のコンポスト化装置において、加圧した酸素含
有気体を給気する給気手段と、吸引せずに排気する排気
手段を交互に縦方向に配置し、最下段の給気手段の位置
が最下段の排気手段の位置よりも下方に配置され、任意
の給気手段の位置とその真上の排気手段の位置との間隔
が、排気手段の真上の給気手段との間隔よりも大きくな
るよう配置されていることを特徴とする生物性有機固形
廃棄物のコンポスト化装置にある。
[3] Biological properties of aerobic fermentation by feeding an oxygen-containing gas to a bed in which moisture-containing granules or moisture-containing coarse particles of biological organic solid waste are continuously filled in the vertical direction. In the organic solid waste composting apparatus, the air supply means for supplying pressurized oxygen-containing gas and the exhaust means for exhausting without suction are alternately arranged in the vertical direction, and the position of the lowermost air supply means Is disposed below the position of the lowermost exhaust means, the interval between the position of any air supply means and the position of the exhaust means directly above it is greater than the distance between the air supply means directly above the exhaust means. An apparatus for composting biological organic solid waste characterized by being arranged to be large.

【0014】上記において、床底面と床上面との間に縦
方向に複数段の給排気手段を配置するのがよい。
In the above, it is preferable to arrange a plurality of stages of supply / exhaust means in the vertical direction between the floor bottom surface and the floor top surface.

【0015】また、前記給排気手段の給気口および排気
口がそれぞれ下向きに開口していることが好ましい。
It is preferable that the air supply and exhaust ports of the air supply and exhaust means open downward.

【0016】また、前記排気口がその下流側に酸素濃度
測定手段を備え、酸素濃度測定手段により測定された酸
素濃度に基づき給気量を制御するようにしてもよい。
Further, the exhaust port may be provided with an oxygen concentration measuring means at a downstream side thereof, and the supply amount may be controlled based on the oxygen concentration measured by the oxygen concentration measuring means.

【0017】また、前記排気口とその直上の給気口との
間隙が0.05〜1m、好ましくは0.1〜0.4mであ
る。
The gap between the exhaust port and the air supply port immediately above the exhaust port is 0.05 to 1 m, preferably 0.1 to 0.4 m.

【0018】さらにまた、任意の床の含水率または任意
の床の排気の湿度を検出し、その直下の給気口の給気量
を制御するようにしてもよい。
Furthermore, the moisture content of an arbitrary floor or the humidity of the exhaust gas of an arbitrary floor may be detected, and the amount of air supplied to an air supply port immediately below the floor may be controlled.

【0019】[0019]

【発明の実施の形態】本発明の特徴は、床底から排気す
る以外に、床底面と床上面との間からも吸引することな
く給気の圧力により槽外に自然に排気し、かつ、床底面
と床上面との間からも給気するようにしたことである。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The feature of the present invention is that, besides exhausting from the floor bottom, the air is naturally exhausted to the outside of the tank by the pressure of the air supply without being sucked from between the floor bottom and the floor upper surface, and That is, air is supplied from between the floor bottom and the floor top.

【0020】本発明の生物性有機固形廃棄物とは、例え
ば、生ごみ、各種の農畜水産廃棄物、醸造廃棄物、水処
理汚泥あるいはこれらの一次発酵コンポストを云う。こ
れらの原料廃棄物に、好ましくは種菌として熟成コンポ
ストを少なくとも0.01%以上添加し、さらに含湿粉
粒体もしくは含湿粗粒体を形成しうる含水率の範囲にな
るように適宜水分を調整後、発酵槽に充填する。
The biological organic solid waste of the present invention refers to, for example, garbage, various agricultural and livestock wastes, brewery waste, water treatment sludge, or primary fermentation compost thereof. To these raw material wastes, at least 0.01% or more of aged compost is preferably added as an inoculum, and water is appropriately added so as to be in a range of a water content at which a wet powder or a wet coarse powder can be formed. After adjustment, fill the fermenter.

【0021】床が高さ2mを超える場合には、発酵槽内
に格子を縦方向に複数段配置すると、床の圧密化を抑制
することができる。発酵が進行する過程で発酵槽底から
床を抜き出し床の上部に返送することにより、床の結着
を防止することができる。
When the height of the floor exceeds 2 m, a plurality of grids are vertically arranged in the fermenter so that the floor can be prevented from being compacted. By pulling out the floor from the bottom of the fermenter and returning it to the upper part of the floor in the course of the progress of the fermentation, the binding of the floor can be prevented.

【0022】また、発酵に必要な含水率20重量%以上
に調整するためには、水または含水率の高い原料を配合
してもよい。原料が粗粒を形成する限界以上に含水率が
高い場合には、低含水率の熟成コンポストや鋸屑、籾
殻、樹皮、コーヒー粕等を添加してもよい。
In order to adjust the water content required for fermentation to 20% by weight or more, water or a raw material having a high water content may be blended. When the water content is higher than the limit at which the raw material forms coarse grains, aging compost having low water content, sawdust, rice husk, bark, coffee grounds, and the like may be added.

【0023】床底面と床上面との間の給排気手段は一組
に限定されず、縦方向に複数組の給排気手段を、所定の
間隔をおいて配置することで、高い床の給排気にも対応
できる。
The air supply / exhaust means between the floor bottom and the floor upper surface is not limited to one set. By arranging a plurality of sets of air supply / exhaust means in the vertical direction at predetermined intervals, air supply / exhaust on a high floor can be achieved. Can also respond.

【0024】また、上記給排気口を下向きに開口するこ
とで閉塞することなく、円滑に給排気ができるので好ま
しい。排気口とその直上の給気口との間隙は、床の物性
や充填高さによって適宜選択することができるが、通常
は0.05〜1m、好ましくは0.1〜0.4mである。
It is preferable that the air supply / exhaust port is opened downward so that air supply / exhaust can be smoothly performed without being closed. The gap between the exhaust port and the air supply port immediately above it can be appropriately selected depending on the physical properties of the floor and the filling height, but is usually 0.05 to 1 m, preferably 0.1 to 0.4 m.

【0025】床間隙が0.05m未満では、給気口から
真下の排気口へ給気の短絡が大きくなり不経済である。
また、床間隙が1mを超えると床への酸素供給が不完全
になり、かつ、圧力損失も大きくなって経済的にも運転
操作上にも不利となる。
If the floor gap is less than 0.05 m, short-circuiting of the air supply from the air supply port to the exhaust port immediately below becomes large, which is uneconomical.
On the other hand, if the bed gap exceeds 1 m, the supply of oxygen to the bed becomes incomplete and the pressure loss increases, which is disadvantageous both economically and in operation.

【0026】[0026]

【実施例】本発明を実施例により説明する。EXAMPLES The present invention will be described with reference to examples.

【0027】〔実施例 1〕図1に本発明の一実施態様
の基本フローを示す。発酵槽1の底部に床底給気口5、
槽の中間の高さに床中間部給気口52、並びに該床中間
部給気口52の約10cm下方に床中間部排気口111
を配置する。
Embodiment 1 FIG. 1 shows a basic flow of an embodiment of the present invention. At the bottom of the fermenter 1, floor bottom air inlet 5,
At the middle height of the tank, the floor middle air inlet 52 and the floor middle air outlet 111 approximately 10 cm below the floor middle air inlet 52.
Place.

【0028】原料有機固形廃棄物と該廃棄物起源コンポ
ストとを混合した粉粒体もしくは粗粒体を、原料供給口
3から槽1内に充填する。空気6をポンプ7、給気配管
8、給気流量調節弁9を経て、床底給気口5と床中間部
吸気口52に分割給気する。
A powder or coarse particles obtained by mixing the raw organic solid waste and the waste-derived compost are filled into the tank 1 through the raw material supply port 3. The air 6 is divided and supplied to the floor bottom supply port 5 and the floor middle section intake port 52 through the pump 7, the supply pipe 8, and the supply flow rate control valve 9.

【0029】床2中を通過し酸素濃度の減少した空気は
排気14として、床中間部排気口111および排気酸素
濃度センサ12、並びに床上排気配管10および排気酸
素濃度センサ12を経て発酵槽1外に排出する。
The air having a reduced oxygen concentration after passing through the floor 2 passes through the middle floor exhaust port 111 and the exhaust oxygen concentration sensor 12 as well as the on-floor exhaust pipe 10 and the exhaust oxygen concentration sensor 12 as the exhaust gas 14, and is discharged outside the fermenter 1. To be discharged.

【0030】排気中の酸素濃度は、排気酸素濃度センサ
12の信号を信号線15で酸素濃度調節器13に伝達し
て測定し、予め設定された酸素濃度の設定値下限に満た
ない場合は、給気量を給気流量調節弁9により増加し、
酸素濃度の設定値上限を超える場合には給気量を給気流
量調節弁9により減少する。
The oxygen concentration in the exhaust gas is measured by transmitting the signal of the exhaust oxygen concentration sensor 12 to the oxygen concentration controller 13 via a signal line 15. If the oxygen concentration is below the preset lower limit of the oxygen concentration, The supply air amount is increased by the supply air flow control valve 9,
If the oxygen concentration exceeds the set upper limit, the supply air amount is reduced by the supply air flow control valve 9.

【0031】槽底給気口5に供給された空気6は、床2
を構成する粉粒体もしくは粗粒体と接触しつつ床中を上
昇し、その大部分は床中間部排気口111から発酵槽1
外に排出される。
The air 6 supplied to the tank bottom air supply port 5 is supplied to the floor 2
Rises in the bed while being in contact with the powdery or coarse particles constituting the fermenter 1.
It is discharged outside.

【0032】残りの床2中の気流は、床中間部給気口5
2から別途供給する空気6と合流し、発酵槽1の上部か
ら排気14として排出する。
The remaining air flow in the floor 2 is supplied to the air inlet 5 in the middle of the floor.
The fermenter 1 joins with the air 6 supplied separately from the fermenter 1, and is discharged from the upper part of the fermenter 1 as exhaust 14.

【0033】上記の給気量制御により、発酵を進行させ
て処理した床を生成コンポストとして発酵槽底のコンポ
スト排出口4から発酵槽1外に排出する。
By the above-described air supply control, the bed treated by progressing the fermentation is discharged as a compost from the compost discharge port 4 at the bottom of the fermenter to the outside of the fermenter 1.

【0034】これによって、生物性有機固形廃棄物の含
湿粉粒体もしくは含湿粗粒体を、高効率で好気発酵する
ことができる。
[0034] Thus, the aerobic fermentation of the moist powder or the coarse moist granules of the biological organic solid waste can be performed with high efficiency.

【0035】〔実施例 2〕図2は、実施例1における
給排気系を3組積層したフロー図である。発酵槽1に充
填した床2の中に発酵槽1の底から上方に向い、床底給
気口5、床中間部給気口52,53,54、並びに、前
記各給気口の約20cm下方に床中間部排気口111,
112,113を配置する。空気6をポンプ7、給気配
管8、給気流量調節弁9を経て床底給気口5、床中間部
給気口52,53,54から分割して供給する。
[Embodiment 2] FIG. 2 is a flow chart in which three sets of supply / exhaust systems in Embodiment 1 are stacked. The floor 2 filled in the fermenter 1 is directed upward from the bottom of the fermenter 1, and the floor bottom air inlet 5, the floor middle air inlets 52, 53, 54, and about 20 cm of each of the above air inlets The lower floor exhaust port 111,
112 and 113 are arranged. The air 6 is supplied separately from the floor bottom supply port 5 and the floor middle supply ports 52, 53, 54 via the pump 7, the supply pipe 8, and the supply flow rate control valve 9.

【0036】空気6は排気14として、各床中間部排気
口111〜113、並びに床上排気配管10および各排
気酸素濃度センサ12を経て発酵槽1外に排出する。各
排気口の酸素濃度は排気酸素濃度センサ12の信号を信
号線15で酸素濃度調節器13に伝達し、予め設定され
た酸素濃度の設定値を超えれば、給気流量調節弁9によ
り給気量を減少し、設定値に満たない場合は給気流量調
節弁9により給気量を増加する。
The air 6 is discharged out of the fermenter 1 through the floor exhaust ports 111 to 113, the floor exhaust pipe 10 and the exhaust oxygen concentration sensors 12 as exhaust 14. The oxygen concentration at each exhaust port is transmitted from an exhaust oxygen concentration sensor 12 to the oxygen concentration controller 13 via a signal line 15 and, if the oxygen concentration exceeds a preset oxygen concentration set value, the supply air flow control valve 9 supplies the oxygen. The amount is reduced, and if less than the set value, the amount of air supply is increased by the air supply flow rate control valve 9.

【0037】発酵槽1の床底給気口5に供給された空気
6は、床2を構成する粉粒体もしくは粗粒体と接触しつ
つ床底給気口5の上部に配置された床中間部排気口11
1から発酵槽1外に排気14として排出される。
The air 6 supplied to the floor bottom air inlet 5 of the fermenter 1 is in contact with the powdery or coarse particles constituting the floor 2 and is placed above the floor bottom air inlet 5. Intermediate exhaust port 11
1 is discharged from the fermenter 1 as exhaust gas 14.

【0038】残りの床中の気流は、床中間部給気口52
から別途供給する空気6と合流して床中を上昇し、その
大部分は床中間部排気口112から発酵槽外に排出され
る。
The remaining airflow in the floor is supplied to the air supply port 52 in the middle of the floor.
From the fermentation tank, and rises up in the bed through the outlet 112 at the middle of the floor.

【0039】さらに残りの床中の気流は床中間部給気口
53から別途供給する空気6と合流して発酵槽中を上昇
し、その大部分は床中間部排気口113から発酵槽外に
排出される。
Further, the remaining air flow in the bed merges with the air 6 supplied separately from the air supply port 53 in the middle of the floor and rises in the fermenter, and most of the air flows out of the fermenter through the exhaust port 113 in the middle of the floor. Is discharged.

【0040】次いで、さらに残りの気流は床中間部給気
口54から別途供給する空気6と合流して床中を上昇
し、床表面に達して、排気14として発酵槽1外に排出
される。
Next, the remaining airflow merges with the air 6 supplied separately from the air supply port 54 in the middle of the floor, rises in the floor, reaches the floor surface, and is discharged out of the fermenter 1 as exhaust 14. .

【0041】上記の給気量制御発酵処理を終えた床を、
生成コンポストとして発酵槽底のコンポスト排出口4か
ら発酵槽1外に排出する。
The floor after the above-described air supply control fermentation treatment is
The resulting compost is discharged out of the fermenter 1 through the compost outlet 4 at the bottom of the fermenter.

【0042】〔実施例 3〕図3は、実施例2において
発酵終了後、または、発酵途中から引き続き給気して床
を乾燥する場合のフローの概略を示す。
[Embodiment 3] FIG. 3 shows an outline of a flow in Example 2 in which air is supplied after the end of fermentation or during the middle of fermentation to dry the bed.

【0043】酸素濃度調節器13の下流に湿度センサ1
6を配置し、発酵から乾燥への切り替えに際し、給気流
量調節弁9への信号を酸素濃度調節器13から湿度調節
器18の信号に切り替える。
The humidity sensor 1 is provided downstream of the oxygen concentration controller 13.
6, the signal to the air supply flow rate control valve 9 is switched from the oxygen concentration controller 13 to the signal from the humidity controller 18 when switching from fermentation to drying.

【0044】湿度センサ16の信号を湿度信号線17に
より湿度調節器18に伝達し、排気の湿度が設定値より
も高い場合、即ち、まだ乾燥が不十分の場合には、給気
流量調節弁9により給気量を増加する。設定値よりも低
い場合、即ち、乾燥が終了すれば給気量を減少もしくは
給気を停止する。
A signal from the humidity sensor 16 is transmitted to a humidity controller 18 via a humidity signal line 17, and when the humidity of the exhaust gas is higher than a set value, that is, when the drying is still insufficient, the supply air flow control valve. 9 to increase the air supply. If the value is lower than the set value, that is, if the drying is completed, the air supply amount is reduced or the air supply is stopped.

【0045】乾燥に用いる給気は外部熱源により加熱し
た床温よりも高い温度の湿度不飽和の気体が好ましい。
The air supplied for drying is preferably a humidity-unsaturated gas having a temperature higher than the bed temperature heated by an external heat source.

【0046】[0046]

【発明の効果】従来の床底のみから給気する発酵方法で
は、床の上部では酸素の欠乏、床の下部では床温の低下
により、床の上下部分の発酵活性が阻害され、また、給
気の圧力損失が大きいため、高い圧力で給気する必要が
あった。
According to the conventional fermentation method in which air is supplied only from the bottom of the bed, the fermentation activity in the upper and lower parts of the bed is inhibited due to lack of oxygen in the upper part of the bed and a decrease in the bed temperature in the lower part of the bed. Because of the large pressure loss of air, it was necessary to supply air at a high pressure.

【0047】本発明によれば、給気を分割供給するのみ
ならず、排気も分割して給気の圧力で自然に発酵槽外に
排出できるため、床中の高さ方向の酸素濃度を発酵に必
要な範囲に維持することができる。
According to the present invention, not only the supply air is divided and supplied, but also the exhaust gas can be divided and naturally discharged to the outside of the fermentation tank at the pressure of the supply air. Can be maintained within the required range.

【0048】さらにまた、給気口当たりの給気量も減少
できるため、給気口近傍での床温度の低下が少なくな
り、床の高さ方向の発酵活性を高水準に維持できる。
Further, since the amount of air supply per air supply port can be reduced, a decrease in the bed temperature near the air supply port is reduced, and the fermentation activity in the height direction of the bed can be maintained at a high level.

【0049】また、給気の圧力損失を減少できるため、
低圧仕様の給気系統および発酵槽を用いることができ、
装置費、運転費を低減できる。
Also, since the pressure loss of the supply air can be reduced,
A low pressure air supply system and fermenter can be used,
Equipment costs and operating costs can be reduced.

【0050】上記に伴い、床高を増加して省面積、か
つ、実用性の高い条件で発酵を高速化することができ
る。
As described above, the fermentation can be speeded up under conditions that save the area by increasing the bed height and are highly practical.

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

【図1】本発明の一実施例の原理フローを示す図であ
る。
FIG. 1 is a diagram showing a principle flow of an embodiment of the present invention.

【図2】本発明の一実施例の原理フローを示す図であ
る。
FIG. 2 is a diagram showing a principle flow of an embodiment of the present invention.

【図3】本発明の一実施例の原理フローを示す図であ
る。
FIG. 3 is a diagram showing a principle flow of an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1…発酵槽、2…床、3…原料供給口、4…コンポスト
排出口、5…床底給気口、52,53,54…床中間部
給気口、6…空気、7…ポンプ、8…給気配管、9…給
気流量調節弁、10…床上排気配管、111,112,
113…床中間部排気口、12…排気酸素濃度センサ、
13…酸素濃度調節器、14…排気、15…信号線、1
6…湿度センサ、17…湿度信号線、18…湿度調節
器。
DESCRIPTION OF SYMBOLS 1 ... Fermentation tank, 2 ... Bed, 3 ... Raw material supply port, 4 ... Compost discharge port, 5 ... Floor bottom supply port, 52, 53, 54 ... Floor middle section supply port, 6 ... Air, 7 ... Pump, 8 ... air supply pipe, 9 ... air supply flow control valve, 10 ... floor exhaust pipe, 111, 112,
113: Floor exhaust port, 12: Exhaust oxygen concentration sensor,
13: oxygen concentration controller, 14: exhaust, 15: signal line, 1
6 ... humidity sensor, 17 ... humidity signal line, 18 ... humidity controller.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 生物性有機固形廃棄物の含湿粉粒体もし
くは含湿粗粒体を、縦方向に連続的に充填した床に酸素
含有気体を給気して好気発酵する生物性有機固形廃棄物
のコンポスト化方法において、 発酵槽の床底面と床上面との間に加圧した酸素含有気体
を給気する給気手段と、吸引せずに排気する排気手段を
設けたことを特徴とする生物性有機固形廃棄物のコンポ
スト化方法。
An aerobic fermentation method in which an oxygen-containing gas is supplied to a bed, which is continuously filled in a longitudinal direction, with a wet powder or a coarse powder of a biological organic solid waste. In the method for composting solid waste, an air supply means for supplying a pressurized oxygen-containing gas between a bottom surface and a floor surface of a fermenter, and an exhaust means for exhausting without suction are provided. Composting method of biological organic solid waste.
【請求項2】 生物性有機固形廃棄物の含湿粉粒体もし
くは含湿粗粒体を、縦方向に連続的に充填した床に酸素
含有気体を給気して好気発酵する生物性有機固形廃棄物
のコンポスト化方法において、 発酵槽の床底面と床上面との間に設けた加圧した酸素含
有気体を給気する給気手段と、吸引せずに排気する排気
手段からも給排気することにより好気発酵させ、発酵処
理後、湿度不飽和の気体を発酵時と同様に給排気して床
を乾燥することを特徴とする生物性有機固形廃棄物のコ
ンポスト化方法。
2. A bioorganic organic compound which aerobically ferments by supplying an oxygen-containing gas to a bed in which a wet powder or a wet coarse powder of a biological organic solid waste is continuously filled in a longitudinal direction. In the method for composting solid waste, air is supplied and exhausted from an air supply means provided between the floor bottom and the floor upper surface of the fermenter to supply pressurized oxygen-containing gas and an exhaust means provided to exhaust without suction. Aerobic fermentation, and after the fermentation treatment, a moisture-unsaturated gas is supplied and exhausted in the same manner as during fermentation to dry the floor, thereby composting a biological organic solid waste.
【請求項3】 生物性有機固形廃棄物の含湿粉粒体もし
くは含湿粗粒体を、縦方向に連続的に充填した床に酸素
含有気体を給気して好気発酵させる生物性有機固形廃棄
物のコンポスト化装置において、 加圧した酸素含有気体を給気する給気手段と、吸引せず
に排気する排気手段を交互に縦方向に配置し、最下段の
給気手段の位置が最下段の排気手段の位置よりも下方に
配置され、任意の給気手段の位置とその真上の排気手段
の位置との間隔が、排気手段の真上の給気手段との間隔
よりも大きくなるよう配置されていることを特徴とする
生物性有機固形廃棄物のコンポスト化装置。
3. A bio-organic material which is subjected to aerobic fermentation by feeding an oxygen-containing gas to a bed, which is continuously filled in the longitudinal direction, with a wet-powder granule or a coarse-grained wet bio-organic solid waste. In a solid waste composting device, an air supply means for supplying pressurized oxygen-containing gas and an exhaust means for exhausting without suction are alternately arranged in the vertical direction, and the position of the lowermost air supply means Arranged below the position of the lowermost exhaust means, the interval between the position of any air supply means and the position of the exhaust means directly above it is greater than the distance between the air supply means directly above the exhaust means. A composting apparatus for biological organic solid waste, wherein the composting apparatus is disposed.
JP10142399A 1998-05-25 1998-05-25 Composting of solid waste from biomass and equipment for that purpose Pending JPH11335192A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10142399A JPH11335192A (en) 1998-05-25 1998-05-25 Composting of solid waste from biomass and equipment for that purpose

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10142399A JPH11335192A (en) 1998-05-25 1998-05-25 Composting of solid waste from biomass and equipment for that purpose

Publications (1)

Publication Number Publication Date
JPH11335192A true JPH11335192A (en) 1999-12-07

Family

ID=15314457

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10142399A Pending JPH11335192A (en) 1998-05-25 1998-05-25 Composting of solid waste from biomass and equipment for that purpose

Country Status (1)

Country Link
JP (1) JPH11335192A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001055295A1 (en) * 2000-01-28 2001-08-02 Alfa Laval Copenhagen A/S Method and apparatus for controlling growth of an organism in a nutrient medium
JP2002248495A (en) * 2001-02-22 2002-09-03 Hitachi Kiden Kogyo Ltd Operation method for excretion residue treatment apparatus
CZ302733B6 (en) * 2010-08-17 2011-10-05 Ceská zemedelská univerzita v Praze System for fermentation of solid biomass
CN102819246A (en) * 2012-07-06 2012-12-12 中环保水务投资有限公司 City domestic sludge compost treatment control system
CN107892592A (en) * 2017-11-28 2018-04-10 上海海和实业有限公司 A kind of reclaiming organic waste handling process

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001055295A1 (en) * 2000-01-28 2001-08-02 Alfa Laval Copenhagen A/S Method and apparatus for controlling growth of an organism in a nutrient medium
JP2002248495A (en) * 2001-02-22 2002-09-03 Hitachi Kiden Kogyo Ltd Operation method for excretion residue treatment apparatus
CZ302733B6 (en) * 2010-08-17 2011-10-05 Ceská zemedelská univerzita v Praze System for fermentation of solid biomass
CN102819246A (en) * 2012-07-06 2012-12-12 中环保水务投资有限公司 City domestic sludge compost treatment control system
CN107892592A (en) * 2017-11-28 2018-04-10 上海海和实业有限公司 A kind of reclaiming organic waste handling process

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