JPH09313874A - Biological deodorizing device - Google Patents

Biological deodorizing device

Info

Publication number
JPH09313874A
JPH09313874A JP8138276A JP13827696A JPH09313874A JP H09313874 A JPH09313874 A JP H09313874A JP 8138276 A JP8138276 A JP 8138276A JP 13827696 A JP13827696 A JP 13827696A JP H09313874 A JPH09313874 A JP H09313874A
Authority
JP
Japan
Prior art keywords
biological
biological deodorizing
filtration layer
water collecting
deodorizing
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.)
Withdrawn
Application number
JP8138276A
Other languages
Japanese (ja)
Inventor
Masanori Yoshinaga
正▲徳▼ 吉永
Isao Osuga
勇雄 大須賀
Takeyoshi Suda
武義 須田
Takeshi Suwa
毅 諏訪
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.)
NIPPON BIO ENG KK
Original Assignee
NIPPON BIO ENG 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 NIPPON BIO ENG KK filed Critical NIPPON BIO ENG KK
Priority to JP8138276A priority Critical patent/JPH09313874A/en
Publication of JPH09313874A publication Critical patent/JPH09313874A/en
Withdrawn legal-status Critical Current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
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Abstract

PROBLEM TO BE SOLVED: To improve an eliminating ratio of an odorous component and also to stably maintain high deodorizing effect for a long period. SOLUTION: In an biological deodorizing tank, plural stages of biological filter layers 41 are provided at the intermediate portions while supported with supporting plates 5, and a water spraying means 42 is arranged at the upper part and an introduction pipe 43 is provided at the lower part. A water collecting recessed groove 51 in the supporting plate 5 is provided on the peripheral part and many communication holes 52 communicated vertically are provided on a plate part of the supporting plate 5 at the inner side than the water collecting groove 51.

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、生ごみ、し尿、下
水、あるいは食品汚泥などから発生する悪臭ガスを分解
して除去する脱臭装置に関するものであって、特に、悪
臭ガス(以下、臭気ガスという)を生化学的に分解する
生物脱臭装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a deodorizing device for decomposing and removing malodorous gas generated from food waste, human waste, sewage, food sludge and the like, and particularly to malodorous gas (hereinafter referred to as malodorous gas). The biological deodorizing device that biochemically decomposes).

【0002】[0002]

【従来の技術】前記生ごみ等から生じる有害な臭気ガス
には、メチルカプタン、硫化水素、硫化メチル、2酸化
メチル、トリメチルアミン、アセトアルデヒド、スチレ
ンなどが代表的であり、これら臭気ガスを除去する装置
が種々提案されている。ここに従来から用いられている
生物脱臭装置の1例を図2によって説明する。
2. Description of the Related Art Methylcaptan, hydrogen sulfide, methyl sulfide, methyl dioxide, trimethylamine, acetaldehyde, styrene and the like are typical examples of harmful odorous gases generated from the above-mentioned garbage, and a device for removing these odorous gases is used. Various proposals have been made. An example of a biological deodorizing device that has been conventionally used will be described with reference to FIG.

【0003】生ごみ、し尿、あるいは食品汚泥などの受
入施設、貯留装置、曝気装置、脱水装置あるいはコンポ
スト化装置などの悪臭源となる悪臭発生源装置1で発生
した臭気ガスはブロワ11によって、洗浄槽2に供給さ
れる。ここで臭気ガスは下方から上方に流れる間に洗浄
槽2に充填されたラヒシリング状のメディア層21を通
過し、ポンプ22によって上方から供給散布される洗浄
水または希釈酸液などの吸収液と接触することによっ
て、主としてアンモニア成分が吸収除去される。なお、
この吸収液は洗浄槽2の下部から取り出され循環使用さ
れる。また、吸収液の吸収性能を調整するためのpH計
(図示せず)などを含む調整装置が設けられている。
The odorous gas generated by the malodorous source device 1 which becomes a malodorous source such as a facility for receiving raw garbage, human waste or food sludge, a storage device, an aeration device, a dehydration device or a composting device is washed by a blower 11. It is supplied to the tank 2. Here, while the odorous gas flows from the lower side to the upper side, the odorous gas passes through a Rahi ring-shaped medium layer 21 filled in the cleaning tank 2 and comes into contact with an absorption liquid such as cleaning water or diluted acid liquid supplied and dispersed by a pump 22 from above. By doing so, mainly the ammonia component is absorbed and removed. In addition,
This absorption liquid is taken out from the lower part of the cleaning tank 2 and is circulated and used. Further, an adjusting device including a pH meter (not shown) for adjusting the absorption performance of the absorbing liquid is provided.

【0004】次いで、臭気ガスは生物脱臭槽3の下部に
導入される。この生物脱臭槽3には、生物脱臭床31が
例えば1.8m〜2.0m厚さに堆積したピートモスな
どで形成されていて、その下方には臭気ガスを導き入れ
る導入管32が設けられ、また上方には散水管33が設
けられている。なおドレンパイプ34が適宜に設けられ
ている。前記洗浄槽2を通った臭気ガスは、導入管32
により生物脱臭床31の下部に導入され、生物脱臭床3
1内を分散し上昇、通過する間に、生物脱臭床31中に
存在する微生物により生化学的に分解され、脱臭される
のである。なお、散水管33は、生物脱臭床31に適宜
散水することで湿度を調節して、臭気ガスを分解する微
生物の棲息環境を適正に保持するためのものである。
Next, the odorous gas is introduced into the lower part of the biological deodorization tank 3. In this biological deodorization tank 3, a biological deodorization bed 31 is formed of, for example, peat moss deposited to a thickness of 1.8 m to 2.0 m, and an introduction pipe 32 for introducing odorous gas is provided below the peat moss. Further, a sprinkler pipe 33 is provided above. A drain pipe 34 is appropriately provided. The odorous gas that has passed through the cleaning tank 2 is introduced into the introduction pipe 32.
Introduced into the lower part of the biological deodorizing bed 31 by
While being dispersed, raised and passed through the inside of 1, the microorganisms in the biological deodorization bed 31 are biochemically decomposed and deodorized. The water sprinkling pipe 33 is used to appropriately control the humidity by sprinkling water on the biological deodorization bed 31 and appropriately maintain the habitat environment of microorganisms that decompose odorous gas.

【0005】ところが、このような生物脱臭装置にあっ
ては、ピートモスなどを堆積してなる生物脱臭床31
は、供用開始から比較的短期間のうちに自重による圧密
によって体積収縮が発生し、例えば6か月程度経過する
と、当初の堆積厚さの80〜85%の厚さに収縮するな
どのように、通気抵抗が増大することの他、収縮に伴い
発生する亀裂に起因する上下連通空間、いわゆるガス道
が、特に前記生物脱臭槽3の内壁面近傍に形成され、か
つ経過時間ととに発達するという現象が認められるので
ある。このため、導入管32からの洗浄臭気ガスはこの
ガス道を下方から上方に脱臭されることなく通過した
り、また散水管33からの散水もそのガス道を上方から
下方に単に通過するようになり、所期の作用効果が得ら
れないという問題があった。
However, in such a biological deodorizing apparatus, a biological deodorizing bed 31 formed by depositing peat moss or the like is used.
Causes volume contraction due to consolidation due to its own weight within a relatively short period from the start of service, and contracts to a thickness of 80 to 85% of the initial deposited thickness after about 6 months, for example. In addition to an increase in ventilation resistance, an upper and lower communication space, a so-called gas passage, which is caused by a crack generated due to contraction, is formed particularly near the inner wall surface of the biological deodorization tank 3 and develops over time. That phenomenon is recognized. Therefore, the cleaning odorous gas from the introduction pipe 32 passes through the gas passage from the lower side to the upper side without being deodorized, and the water sprinkling from the sprinkling pipe 33 simply passes through the gas passage from the upper side to the lower side. Therefore, there is a problem in that the desired effect cannot be obtained.

【0006】すなわち、臭気ガスの通路が短絡し通過量
が偏在することから、臭気成分の高い除去率が得られな
い、また負荷変動に対応しにくいことになる。また、均
等な調湿が困難となり、ピートモスの部分的乾燥化が進
行して臭気ガスを分解する微生物の棲息環境が悪化す
る、さらには乾燥が進んで撥水性が現れると調湿が一層
困難となり微生物の代謝を阻害するという悪循環に陥
り、脱臭効果を長期にわたって安定に維持することが困
難となる。
That is, since the passage of the odorous gas is short-circuited and the passing amount is unevenly distributed, a high removal rate of the odorous component cannot be obtained and it is difficult to cope with the load fluctuation. In addition, it becomes difficult to evenly control the humidity, and the partial drying of peat moss progresses to deteriorate the habitat environment of microorganisms that decompose odorous gas. A vicious cycle of inhibiting the metabolism of microorganisms occurs, making it difficult to maintain a stable deodorizing effect for a long period of time.

【0007】[0007]

【発明が解決しようとする課題】本発明は、上記の問題
点を解決するためになされたものであり、臭気成分の除
去率を向上させるとともに、高い脱臭効果を長期にわた
って安定に維持することが可能となる生物脱臭装置を提
供する。
SUMMARY OF THE INVENTION The present invention has been made to solve the above problems, and it is possible to improve the removal rate of odorous components and maintain a high deodorizing effect stably for a long period of time. A biological deodorizing device that can be used.

【0008】[0008]

【課題を解決するための手段】上記の問題は、中間には
支持板に支持され、臭気ガス成分を分解する微生物を担
持させた生物濾過層と、上方には該生物濾過層を調湿す
るための散水手段と、下方には臭気ガスを導入するため
の導入管を有する生物脱臭槽を含む生物脱臭装置におい
て、前記生物濾過層が間隔を設けて複数段配設されると
ともに、前記支持板の周辺部には集水凹溝が設けられ、
その集水溝より内側の板部には上下に連通した多数の連
通孔が設けられていることを特徴とする生物脱臭装置に
より解決することができる。
[Means for Solving the Problems] The above problems are caused by a biological filter layer supported in the middle by a supporting plate and carrying microorganisms for decomposing odorous gas components, and a biological filter layer above the biological filter layer for controlling humidity. In a biological deodorizing apparatus including a biological deodorizing tank having a water sprinkling means for lowering and an odorous gas introducing pipe below, the biological filter layers are arranged in a plurality of stages at intervals, and the supporting plate is provided. A water collecting groove is provided around the
This can be solved by the biological deodorizing device characterized in that the plate portion inside the water collecting groove is provided with a large number of communication holes that communicate vertically.

【0009】[0009]

【発明の実施の形態】次に、本発明の実施形態の1例を
図1のフロー図によって説明する。悪臭源となる悪臭発
生源装置1からの臭気ガスはブロワ11によって、洗浄
槽2に供給され、ここで臭気ガス中の主としてアンモニ
ア成分が、ポンプ22によって上方から供給散布される
吸収液によって吸収除去されるよう構成されているの
は、従来例と同様である。
BEST MODE FOR CARRYING OUT THE INVENTION Next, an example of an embodiment of the present invention will be described with reference to the flowchart of FIG. The odorous gas from the malodorous source device 1, which is a malodorous source, is supplied to the cleaning tank 2 by the blower 11, where mainly the ammonia component in the odorous gas is absorbed and removed by the absorption liquid supplied from above by the pump 22. It is the same as the conventional example.

【0010】次いで、臭気ガスは生物脱臭槽3の下部に
導入されることになるが、この生物脱臭槽3には、中間
部分に臭気ガス成分を分解する微生物を担持させた生物
濾過層41が支持板5に支持された形態で複数段(この
実施形態では3段となっている)設けられている。この
生物濾過層41は、垂直方向に間隔を設けて好ましくは
3〜5段の複数段に設けられていて、それぞれがピート
モス、炭、活性炭あるいは珊瑚片などの充填材を単独に
またはその複数を適宜に組み合わせて積層状または混合
物状にして、厚さが1.5m以下、好ましくは0.5〜
1.0mの厚さに堆積されたものである。
Next, the odorous gas is introduced into the lower part of the biological deodorization tank 3. In the biological deodorization tank 3, a biological filtration layer 41 carrying microorganisms for decomposing the odorous gas component is provided in an intermediate portion. A plurality of stages (three stages in this embodiment) are provided while being supported by the support plate 5. The biological filtration layer 41 is provided in a plurality of stages, preferably 3 to 5 stages, with a space provided in the vertical direction, and each of them is a peat moss, charcoal, activated carbon, or a filler such as coral pieces alone or a plurality thereof. The layers are appropriately combined to form a laminate or a mixture and have a thickness of 1.5 m or less, preferably 0.5 to
It was deposited to a thickness of 1.0 m.

【0011】また、上方には該生物濾過層41に水分を
補給して調湿するためのスプレーノズルなどの散水手段
42が配設され、下方には臭気ガスを導入するための導
入管43が配設されている。
Further, a spraying means 42 such as a spray nozzle for replenishing the biological filtration layer 41 with water to control the humidity is arranged above, and an introducing pipe 43 for introducing odorous gas is provided below. It is arranged.

【0012】そして、生物濾過層41を支持している前
記支持板5には、その周辺部に、生物脱臭槽3の内壁面
に沿って集水凹溝51が設けられ、この集水凹溝51か
ら適宜に排水するためのドレンノズル53が生物脱臭槽
3の壁体から突出して設けられている。さらに、この集
水凹溝51より内側の支持板5の板部には多数の連通孔
52が設けられていて、支持板5上の生物濾過層41と
支持板5下の空間とが連絡している。
The support plate 5 supporting the biological filtration layer 41 is provided with a water collecting groove 51 at the peripheral portion thereof along the inner wall surface of the biological deodorizing tank 3. A drain nozzle 53 for appropriately draining water from 51 is provided so as to project from the wall of the biological deodorization tank 3. Further, a large number of communication holes 52 are provided in the plate portion of the support plate 5 inside the water collecting groove 51, and the biological filtration layer 41 on the support plate 5 and the space under the support plate 5 communicate with each other. ing.

【0013】このような生物脱臭装置の動作を説明す
る。悪臭発生源施設1から導出された臭気ガスは洗浄槽
2でアンモニア成分が除去されて、導入管43から生物
脱臭槽4の最下段の支持板5下の空間に供給される。そ
こで、臭気ガスは最下段の支持板5に設けられている連
通孔52を通って上方の生物濾過層41に導かれ、そこ
を通過するときに生物濾過層41に担持された脱臭微生
物により、メチルメルカプタン、硫化メチル、トリメチ
ルアミンなどの臭気成分が生化学的に分解されるのであ
る。次いで、これら臭気ガスは、2段目生物濾過層41
さらには3段目の生物濾過層41に同様に導かれるの
で、脱臭作用が繰り返して行われ、臭気ガスの無害化が
達成されるのである。この場合、生物濾過層41内を臭
気ガスが通過する速度は30〜80cm/秒、好ましく
は40〜60cm/秒である。
The operation of such a biological deodorizer will be described. The odorous gas derived from the foul-smelling source facility 1 is cleaned of ammonia components in the cleaning tank 2 and supplied from the introduction pipe 43 to the space below the lowermost support plate 5 of the biological deodorizing tank 4. Therefore, the odorous gas is guided to the upper biological filtration layer 41 through the communication holes 52 provided in the lowermost support plate 5, and when passing through the deodorizing microorganisms carried on the biological filtration layer 41, Odor components such as methyl mercaptan, methyl sulfide and trimethylamine are biochemically decomposed. Next, these odorous gases are used as the second biological filtration layer 41.
Furthermore, since it is similarly guided to the third-stage biological filtration layer 41, the deodorizing action is repeatedly performed, and the deodorization of the odorous gas is achieved. In this case, the speed at which the odorous gas passes through the biological filtration layer 41 is 30 to 80 cm / sec, preferably 40 to 60 cm / sec.

【0014】一方、生物濾過層41の上方に設けられた
にスプレーノズルなどの散水手段42から散水された調
湿水は、最上段の生物濾過層41に浸透し均等に湿潤さ
せ、次いで過剰な水分の一部は、支持板5の多数の連通
孔52を通じて順次下段の生物濾過層41に滴下し、以
下同様にして最下段の生物濾過層41まで湿潤させると
ともに、過剰な水分の残部は、生物脱臭槽3の内壁面に
沿って、支持板5の周辺部に設けられた集水凹溝51に
集められて、一旦滞留することになる。この場合、生物
濾過層41の一部はこの滞留している調湿水に接触して
いるので、生物濾過層41が乾燥してくるとこの滞留調
湿水によって自動的に給水されるから、生物濾過層41
は常に過不足なく調湿されることになる。そして、不要
となった過剰水分は最終的にドレン水としてドレンノズ
ル53から排出される。
On the other hand, the humidity control water sprinkled from the water spraying means 42 such as a spray nozzle provided above the biological filtration layer 41 permeates the biological filtration layer 41 at the uppermost stage to evenly moisten it, and then an excessive amount of water. Part of the water content is sequentially dropped onto the biological filtration layer 41 in the lower stage through a large number of communication holes 52 of the support plate 5, and in the same manner as above, the biological filtration layer 41 in the lowermost stage is wetted, and the remainder of the excess water is Along the inner wall surface of the biological deodorization tank 3, the water is collected in the water collecting groove 51 provided in the peripheral portion of the support plate 5 and temporarily stays. In this case, since a part of the biological filtration layer 41 is in contact with the staying humidity-controlling water, when the biological filtration layer 41 becomes dry, the staying humidity-controlling water automatically supplies water. Biological filtration layer 41
Will always be conditioned with just enough. Then, the unnecessary excess water is finally discharged from the drain nozzle 53 as drain water.

【0015】本発明の生物脱臭装置は以上説明したよう
な構造を備えているので、生物濾過層41は常に適正に
調湿されているから、臭気成分を除去する微生物の棲息
環境が常に良好に維持されるとともに、生物脱臭槽3の
内壁面近傍にガス道が形成されることが少なく、また局
部的に乾燥が進行して撥水性が顕在化するという欠陥も
生じないことと併せて、臭気ガスはそのような生物濾過
層41を複数段通過することによって、臭気成分の除去
が効率よく行われるとともに、優れた脱臭効果が長期間
維持されるるのである。
Since the biological deodorizing apparatus of the present invention has the structure described above, since the biological filtration layer 41 is always properly controlled in humidity, the habitat of microorganisms for removing odorous components is always good. In addition to being maintained, a gas passage is rarely formed in the vicinity of the inner wall surface of the biological deodorizing tank 3, and the defect that the water repellency becomes apparent due to the local progress of drying is not generated. The gas passes through such a biological filtration layer 41 in a plurality of stages, so that the odorous components are efficiently removed and an excellent deodorizing effect is maintained for a long period of time.

【0016】さらに、好ましくは図1に示されるよう
に、前記支持板5の周辺部から中央に向かって高さが高
くなる段部54とそれに続く平坦部を設け、その平坦部
に前記の多数の連通孔52を設けるよう具体化するのが
よい。このように構成したものは、下方から導かれる臭
気ガスが前記平坦部の裏面に順次自動的に集められ、生
物濾過層41の底部から上昇浸透させることができると
ともに、生物濾過層41の周辺部分は集水凹溝51に滞
留している調湿水と広い面積で接触することができるか
ら、生物濾過層41はより適度に調湿されるので、生物
脱臭槽3の内壁面近傍にガス道が生じ難く、仮にガス道
が生じたとしても臭気ガスの通路とは交差しないので脱
臭効果が低下しにくいという利点がある。
Further, preferably, as shown in FIG. 1, a step portion 54 having a height increasing from the peripheral portion to the center of the supporting plate 5 and a flat portion following the step portion 54 are provided, and the flat portion has the above-mentioned plurality of portions. It is preferable to embody it so as to provide the communication hole 52. With this structure, the odorous gas introduced from below can be automatically collected on the back surface of the flat portion in order to increase and permeate from the bottom of the biological filtration layer 41 and the peripheral portion of the biological filtration layer 41. Can contact the humidity control water staying in the water collecting groove 51 over a wide area, so that the biological filtration layer 41 is more appropriately controlled in humidity, so that the gas passage is formed near the inner wall surface of the biological deodorization tank 3. Is less likely to occur, and even if a gas passage occurs, it does not intersect with the passage of odorous gas, so that the deodorizing effect is less likely to decrease.

【0017】また、前記の生物脱臭層4において、前記
支持板の周辺部に設けられた集水溝51の外周壁を前記
生物脱臭槽4の壁体によって形成するよう具体化する
と、構造が簡単となる利点がある。また、前記生物濾過
層41を、層の厚さが1.5m以下の堆積したピートモ
スで形成すると、調湿水を吸水した状態でも、自重によ
る圧密の程度が少なく、通気抵抗が顕著には増大しない
から、臭気ガスの通過を阻害せず、また槽3の内面近傍
にガス道が生じにくいので特に好ましい。
In the biological deodorizing layer 4, if the outer peripheral wall of the water collecting groove 51 provided in the peripheral portion of the support plate is formed by the wall of the biological deodorizing tank 4, the structure is simple. There is an advantage to be. Further, when the biological filtration layer 41 is formed of deposited peat moss having a layer thickness of 1.5 m or less, the degree of consolidation due to its own weight is small and the ventilation resistance is remarkably increased even in the state where the humidity control water is absorbed. This is particularly preferable because it does not hinder the passage of odorous gas and a gas passage is unlikely to occur near the inner surface of the tank 3.

【0018】次に、本発明の生物脱臭装置の脱臭性能を
表1、表2に示す。表1は、供用開始20日後の従来例
と本発明の装置による脱臭性能を比較したものである。
ここで原ガスは、し尿酸化処理汚泥4t、食品汚泥4
t、畜腹糞1tおよび鋸粉1tの混合物を原料にした処
理日量10tのコンポスト化装置から導出された原臭気
ガスを稀硫酸で洗浄処理しアンモニア成分を除去し、洗
浄槽3の出口で採取したものである。表2は、同じく供
用開始6か月後のものである。なお、従来例の装置は、
厚さ1.8mの生物脱臭床31を備えた図2に示す構
造、本発明の装置は、厚さ0.9mの生物濾過層41を
3段備えた図1に示す構造からなる生物脱臭層41を備
えたものである。
Next, Tables 1 and 2 show the deodorizing performance of the biological deodorizing apparatus of the present invention. Table 1 compares the deodorizing performances of the conventional example and the device of the present invention 20 days after the start of service.
Here, the raw gas is 4t of human waste oxidation-treated sludge and 4 of food sludge.
At the outlet of the cleaning tank 3, the raw odor gas derived from a composting device with a daily processing amount of 10 t, which is made of a mixture of t, litter of dung and 1 t of sawdust, is washed with diluted sulfuric acid to remove ammonia components. It was collected. Table 2 is also 6 months after the start of operation. In addition, the device of the conventional example,
The structure shown in FIG. 2 provided with a biological deodorization bed 31 having a thickness of 1.8 m, the apparatus of the present invention is a biological deodorization layer having the structure shown in FIG. 1 provided with three stages of biological filtration layers 41 having a thickness of 0.9 m. 41 is provided.

【0019】[0019]

【表1】 [Table 1]

【0020】[0020]

【表2】 [Table 2]

【0021】この表1、表2から明らかなように、従来
例の生物脱臭装置では、個々の臭気成分の脱臭率は、5
0〜90%の程度にとどまり、かつ経時的に脱臭率の低
下が認められ、長期安定性に問題があることが示されて
いるが、本発明の生物脱臭装置において、処理後の臭気
成分の濃度は大部分の成分が測定不可(ND)の極低値
となっており、かつ6か月後においても経時変化が殆ど
認められないというように、長期に安定した脱臭効果が
確認された。
As is clear from Tables 1 and 2, in the conventional biological deodorizing apparatus, the deodorizing rate of each odor component is 5
It is shown that the deodorization rate remains in the range of 0 to 90%, and that there is a problem with long-term stability. However, in the biological deodorization apparatus of the present invention, the odor components after treatment are Most of the components had extremely low values (ND), which were not measurable (ND), and almost no change with time was observed even after 6 months, confirming a stable deodorizing effect for a long period of time.

【0022】なお、本発明は図1の形態に限定されるも
のではなく、例えば脱臭槽の形状は、円形、楕円形、四
角形ほか多角形の水平断面形状、あるいは三角形、矩
形、砲弾形状、蒲鉾形状の縦断面形状など各種のもので
もよく、生物濾過層の材質、堆積厚さなどは各段ごとに
異ならせたものでもよく、また、支持板の段部形状はシ
ルクハット型、シリンドリカル型、コニカル型などであ
ってもよい。さらに支持板の連通孔は、パンチングメタ
ル板、金網板などから形成されたものでもよく、この連
通孔を設けた支持板上面には、点々状または溝状の凹凸
を設けたり、支持板には、ドレン引き抜き高さを調節す
る装置を付設することもできる。
The present invention is not limited to the embodiment shown in FIG. 1. For example, the shape of the deodorizing tank is a circular, elliptical, quadrangular or other polygonal horizontal cross-sectional shape, or a triangle, a rectangle, a shell shape, or a kamaboko. Various shapes such as vertical cross-sectional shape may be used, the material of the biological filtration layer, the deposition thickness may be different for each step, and the step shape of the support plate may be a top hat type, a cylindrical type, It may be a conical type or the like. Further, the communication hole of the support plate may be formed of a punching metal plate, a wire mesh plate, or the like. A device for adjusting the drain withdrawal height can be attached.

【0023】[0023]

【発明の効果】本発明の生物脱臭装置は、以上に説明し
たように構成されているので、臭気成分の除去率を向上
させるとともに、高い脱臭効果を長期にわたって安定に
維持することができる。また、本発明の生物脱臭装置
は、小型軽量、プレハブ化が可能であり組立、分解、移
設が容易であることから、省スペース、省エネルギーと
立地条件の緩和あるいは建設費の節減が図られるという
優れた効果がある。よって本発明は従来の問題点を解消
した生物脱臭装置として、その工業的価値が極めて大な
るものがある。
Since the biological deodorizing apparatus of the present invention is constructed as described above, it is possible to improve the removal rate of odorous components and maintain a high deodorizing effect stably for a long period of time. In addition, the biological deodorizer of the present invention is small and lightweight, can be prefabricated, and is easy to assemble, disassemble, and relocate, so it is excellent in that it saves space, saves energy, eases site conditions, and saves construction costs. There is an effect. Therefore, the present invention has an extremely great industrial value as a biological deodorizing device that solves the conventional problems.

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

【図1】本発明の実施形態を説明するための要部断面を
含むフロー図。
FIG. 1 is a flow chart including a cross section of a main part for explaining an embodiment of the present invention.

【図2】従来例を示す要部断面を含むフロー図。FIG. 2 is a flowchart including a cross section of a main part of a conventional example.

【符号の説明】[Explanation of symbols]

1 悪臭発生源装置、2 洗浄槽、3 生物脱臭槽、4
1 生物濾過層、42散水手段、43、導入管、5 支
持板、51 集水凹溝、52 連通孔。
1 odor source device, 2 cleaning tank, 3 biological deodorizing tank, 4
1 biological filtration layer, 42 water sprinkling means, 43, introduction pipe, 5 support plate, 51 water collecting groove, 52 communication hole.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 諏訪 毅 愛知県名古屋市港区善進町4丁目11番地 グランドメゾンフジ202号 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Takeshi Suwa 4-11, Zenshin-cho, Minato-ku, Nagoya, Aichi Prefecture Grand Maison Fuji No. 202

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 中間には支持板に支持され、臭気ガス成
分を分解する微生物を担持させた生物濾過層と、上方に
は該生物濾過層を調湿するための散水手段と、下方には
臭気ガスを導入するための導入管を有する生物脱臭槽を
含む生物脱臭装置において、前記生物濾過層が間隔を設
けて複数段配設されるとともに、前記支持板の周辺部に
は集水凹溝が設けられ、その集水凹溝より内側の板部に
は上下に連通した多数の連通孔が設けられていることを
特徴とする生物脱臭装置。
1. A biological filtration layer supported in the middle by a support plate and supporting microorganisms for decomposing odorous gas components, a sprinkling means for controlling the humidity of the biological filtration layer in the upper part, and a lower part in the lower part. In a biological deodorizing device including a biological deodorizing tank having an introduction pipe for introducing an odorous gas, the biological filtering layers are arranged in a plurality of stages at intervals, and a water collecting groove is provided in a peripheral portion of the supporting plate. The biological deodorizing device is characterized in that a plate portion inside the water collecting groove is provided with a plurality of communication holes that communicate with each other in the vertical direction.
【請求項2】 前記支持板の周辺部から中央に向かって
高さが高くなる段部とそれに続く平坦部が設けられ、そ
の平坦部には前記の連通孔が設けられている請求項1に
記載の生物脱臭装置。
2. The stepped portion, the height of which increases from the peripheral portion of the support plate toward the center, and the flat portion that follows the stepped portion are provided, and the flat portion is provided with the communication hole. The biological deodorizing device described.
【請求項3】 前記集水凹溝の外周壁が前記生物脱臭槽
の壁体によって形成されている請求項1または2に記載
の生物脱臭装置。
3. The biological deodorizing apparatus according to claim 1, wherein an outer peripheral wall of the water collecting groove is formed by a wall body of the biological deodorizing tank.
【請求項4】 前記生物濾過層の厚さが1.5m以下で
ある請求項1から3のいずれかに記載のの生物脱臭装
置。
4. The biological deodorizing apparatus according to claim 1, wherein the biological filtration layer has a thickness of 1.5 m or less.
JP8138276A 1996-05-31 1996-05-31 Biological deodorizing device Withdrawn JPH09313874A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8138276A JPH09313874A (en) 1996-05-31 1996-05-31 Biological deodorizing device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8138276A JPH09313874A (en) 1996-05-31 1996-05-31 Biological deodorizing device

Publications (1)

Publication Number Publication Date
JPH09313874A true JPH09313874A (en) 1997-12-09

Family

ID=15218139

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8138276A Withdrawn JPH09313874A (en) 1996-05-31 1996-05-31 Biological deodorizing device

Country Status (1)

Country Link
JP (1) JPH09313874A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007203149A (en) * 2006-01-31 2007-08-16 Yuji Osuga Biological deodorization tank
KR100883448B1 (en) * 2008-03-18 2009-02-11 비티코리아주식회사 Apparatus for deodorizing fermentation gas of garbage process
JP2010082594A (en) * 2008-10-02 2010-04-15 National Agriculture & Food Research Organization Environmental control method and device for organism deodorizing
CN113058398A (en) * 2021-03-25 2021-07-02 中国城市建设研究院有限公司 Movable integrates biological deodorization system
KR20230027370A (en) * 2021-08-18 2023-02-28 주식회사 에이치앤엠바이오 Organic Waste Treatment Odor Removal Device

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007203149A (en) * 2006-01-31 2007-08-16 Yuji Osuga Biological deodorization tank
JP4653667B2 (en) * 2006-01-31 2011-03-16 勇治 大須賀 Biological deodorization tank
KR100883448B1 (en) * 2008-03-18 2009-02-11 비티코리아주식회사 Apparatus for deodorizing fermentation gas of garbage process
JP2010082594A (en) * 2008-10-02 2010-04-15 National Agriculture & Food Research Organization Environmental control method and device for organism deodorizing
CN113058398A (en) * 2021-03-25 2021-07-02 中国城市建设研究院有限公司 Movable integrates biological deodorization system
CN113058398B (en) * 2021-03-25 2022-07-05 中国城市建设研究院有限公司 Movable integrates biological deodorization system
KR20230027370A (en) * 2021-08-18 2023-02-28 주식회사 에이치앤엠바이오 Organic Waste Treatment Odor Removal Device

Similar Documents

Publication Publication Date Title
US6069004A (en) Circulatory microorganic deodorizing system
US6168711B1 (en) Water supply and drainage type microorganic deodorizing system
CN106799164A (en) A kind of two-phase biologic deodorization method and odor removal
DE3428798A1 (en) Apparatus for purifying exhaust gas
JPH09313874A (en) Biological deodorizing device
JP2003033625A (en) Biological deodorizing method
KR0138050B1 (en) Method and apparatus for biological deordorization of flue gas
JP2697066B2 (en) Biological deodorizer
JPH08131761A (en) Filling type biological deodorization apparatus
JP3063103B2 (en) Biological deodorization method
JP2000041670A (en) Deodorizing system and deodorizing apparatus
CN214513773U (en) Odor treatment device and rainwater regulation and storage tank using same
CN219744435U (en) Deodorization facility
JPH05168850A (en) Biologically deodorizing method
JP3500694B2 (en) Biological deodorizer
JP2001038143A (en) Deodorizing device
JP2002079050A (en) Deodorizing method and apparatus
CN220478533U (en) Multiphase biodegradation odor treatment system
JPH0711783Y2 (en) Biological deodorizer
KR101147403B1 (en) Soil Deodorizing Structure
JP4614875B2 (en) Biological deodorization equipment
JPH10216468A (en) Covering device having biological deodorizing function
JPH0646999B2 (en) Odorous gas biological treatment equipment
JP2008189527A (en) Method of deodorization of compost and apparatus for deodorization of compost
JPH09267022A (en) Deodorizing method

Legal Events

Date Code Title Description
A300 Withdrawal of application because of no request for examination

Free format text: JAPANESE INTERMEDIATE CODE: A300

Effective date: 20030805