JPH09313871A - Horizontal biological deodorizing device - Google Patents

Horizontal biological deodorizing device

Info

Publication number
JPH09313871A
JPH09313871A JP8159274A JP15927496A JPH09313871A JP H09313871 A JPH09313871 A JP H09313871A JP 8159274 A JP8159274 A JP 8159274A JP 15927496 A JP15927496 A JP 15927496A JP H09313871 A JPH09313871 A JP H09313871A
Authority
JP
Japan
Prior art keywords
biological
gas
water
microbial
treatment tank
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
JP8159274A
Other languages
Japanese (ja)
Inventor
Tadataka Takagawa
恭敬 高川
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.)
Mitsubishi Kakoki Kaisha Ltd
Original Assignee
Mitsubishi Kakoki Kaisha 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 Mitsubishi Kakoki Kaisha Ltd filed Critical Mitsubishi Kakoki Kaisha Ltd
Priority to JP8159274A priority Critical patent/JPH09313871A/en
Publication of JPH09313871A publication Critical patent/JPH09313871A/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
    • 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

Landscapes

  • Treating Waste Gases (AREA)

Abstract

PROBLEM TO BE SOLVED: To obtain a biological deodorizing device free from the generation of channeling or short pass, capable of decreasing the height and reducing floor space by providing a microorganism adherent material made of a long sized fiber having no space in the upper end and dipped into water in the lower end in the inside of a biological treating vessel. SOLUTION: A feed port 5 for a gas to be treated and a discharge port 6 for the gas to be treated are provided respectively at one end side and another end side in the longitudinal direction of the horizontally long rectangular biological treating vessel 1. And many long sized fiber made biological adherent material 10, the upper end of which is fixed with a fixing member to the upper wall of the vessel 1 so as not to generate the space between the upper end and the upper wall of the vessel 1 and the lower end of which is hung down as a free end, is provided over almost whole cross sectional surface so as to cross to the passing direction of the gas to be heated. And a washing water is sprayed by a spray means 3 on the biological adherent material 2 and the water level of a trap part 4 is controlled so that the lower end of the biological adherent material 2 is dipped into water. Thus, the biological deodorizing device is formed into the horizontal type, the floor space is reduced and the height is decreased and the pressure loss is low and the deodorization efficiency is improved.

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】本発明は下水処理場、し尿処
理場及び各種工場から排出される悪臭ガス中の悪臭成分
を生物学的に分解して脱臭処理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 biological deodorizing apparatus for biologically decomposing malodorous components in malodorous gas discharged from sewage treatment plants, human waste treatment plants and various factories.

【0002】[0002]

【従来の技術】上記下水やし尿処理場等から発生する悪
臭ガス中の悪臭成分は、主に、硫化水素、メチルメルカ
プタン、硫化メチル、2硫化メチル等の硫黄化合物、及
びアンモニア等である。
2. Description of the Related Art Malodorous components in malodorous gas produced from the above-mentioned sewage and night soil treatment plants are mainly hydrogen sulfide, methyl mercaptan, sulfur compounds such as methyl sulfide and methyl disulfide, and ammonia.

【0003】上記物質は微生物によって分解することが
できるため、悪臭成分を分解する微生物を着生保持する
微生物着生部を内設した生物処理槽により悪臭ガスを脱
臭処理する生物脱臭装置が使用されている。
Since the above substances can be decomposed by microorganisms, a biological deodorizer for deodorizing malodorous gas is used by a biological treatment tank having a microorganism-depositing part for retaining and accumulating microorganisms decomposing malodorous components. ing.

【0004】尚、上記微生物を着生する微生物着生材と
しては、表面積が大きく微生物の着生、繁殖が良好に行
われ、脱臭効率を長期間高く維持することができる材料
が好ましく、長繊維束、土壌、ピ−ト、多孔質セラミッ
クス及び活性炭等が主に使用されている。
[0004] As the microbial engraftment material for engrafting the above-mentioned microorganisms, a material having a large surface area, in which the microorganisms can be well established and propagated, and which can maintain a high deodorizing efficiency for a long time, is preferable. Bundles, soils, peats, porous ceramics and activated carbon are mainly used.

【0005】また、微生物着生部においては、悪臭成分
の生物学的酸化分解によって生成される酸性成分により
PHが低下して微生物の生育を阻害させる恐れがあるた
め、生成物を洗浄除去すると共に、微生物の棲息に必要
な水分を補給する等のため適宜に散水洗浄している。
In addition, in the microbial engraftment part, the acidic component produced by the biological oxidative decomposition of the malodorous component may lower the pH and inhibit the growth of the microorganism, so that the product should be washed and removed. , Water is appropriately washed to replenish the water necessary for habitation of microorganisms.

【0006】尚、散水洗浄に使用される洗浄水として
は、汚水の活性汚泥処理水、河川水又は地下水などが一
般的に用いられており、また散水洗浄は連続散水又は所
定の時間間隔による間欠散水により行われている。
As the cleaning water used for the water spray cleaning, activated sludge treated water of sewage, river water, groundwater, etc. are generally used, and the water spray cleaning is either continuous water spraying or intermittent spraying at predetermined time intervals. It is done by watering.

【0007】従来の生物脱臭装置としては、高い生物処
理槽内に微生物を担持した微生物着生部を高さ方向に1
段又は複数段設け、単一の洗浄手段により散水洗浄する
生物脱臭装置が一般的に用いられている。
As a conventional biological deodorizing apparatus, a microbial growth part supporting microorganisms in a high biological treatment tank is provided in a height direction of 1
A biological deodorizing device is generally used, which is provided with stages or a plurality of stages and is spray-washed by a single washing means.

【0008】また、生物処理槽を複数基設け、管路で直
列に連接した生物脱臭装置(特開平5−115742
号)や水平横長の生物処理槽内に1段の水平横長微生物
着生部を設け、多段の洗浄手段により散水洗浄する生物
脱臭装置(特開平4−363111号)等も知られてい
る。
Further, a plurality of biological treatment tanks are provided, and a biological deodorizing device connected in series through a pipeline (Japanese Patent Laid-Open No. 5-115742).
No.) or a horizontally elongated biological treatment tank, and a biological deodorizing device (Japanese Unexamined Patent Publication No. 4-363111) in which a horizontal horizontally microbial colonization section is provided in one stage and water is sprayed and washed by a multi-stage cleaning means.

【0009】[0009]

【発明が解決しようとする課題】上記従来の生物脱臭装
置において、高い生物処理槽内の高さ方向に複数段の微
生物着生部を設け、単一の洗浄手段で散水洗浄する生物
脱臭装置にあっては、一般的に限定された時間内に一定
量の散水量が必要であり、段数が増加するに従って洗浄
水の供給量を多くするため、下段になるほど洗浄水量が
多くなり、微生物及び脱臭効率に与える影響は無視でき
ない。
In the above-mentioned conventional biological deodorizing apparatus, a biological deodorizing apparatus is provided in which a plurality of stages of microbial growth portions are provided in a height direction in a high biological treatment tank and water is washed by a single washing means. However, in general, a certain amount of water is required within a limited time, and as the number of stages increases, the amount of wash water supplied increases. The effect on efficiency cannot be ignored.

【0010】また、微生物着生部を高さ方向に区画して
複数段の微生物着生部を設けたとしても、段数が多くな
るに従って当然生物処理槽の高さも高くなり、屋内など
高さをできるだけ低くおさえる必要がある場所では、設
置段数に限界があり、段数を増加させて脱臭効果を上げ
ることができない欠点がある。
Further, even if the microbial growth portion is divided in the height direction and a plurality of stages of microbial growth portion are provided, the height of the biological treatment tank naturally increases as the number of stages increases, so that the height of the indoor treatment chamber is increased. In places where it is necessary to keep the temperature as low as possible, there is a limit to the number of stages that can be installed, and there is the disadvantage that the number of stages cannot be increased to improve the deodorizing effect.

【0011】更に、複数基の生物処理槽を管路で直列に
連接した特開平5−115742号に記載された生物脱
臭装置にあっては、生物処理槽を多く設ける程、配管な
どの付帯設備の面積も広く必要となり、装置全体の設置
面積が必要以上に広大となると共に装置構成も複雑とな
る。
Further, in the biological deodorizing apparatus described in Japanese Patent Laid-Open No. 5-115742, in which a plurality of biological treatment tanks are connected in series by pipelines, the more biological treatment tanks are provided, the more ancillary equipment such as piping. Requires a large area, and the installation area of the entire apparatus becomes unnecessarily large and the apparatus configuration becomes complicated.

【0012】また水平横長の生物処理槽内に1段の水平
横長微生物着生部を設けた特開平4−363111号に
記載された生物脱臭装置にあっては、微生物着生部の上
方に設けた散水手段の配置部や下方の液溜まり部で、被
処理ガスがショ−トパスして脱臭効率が低くなる欠点が
ある。
Further, in the biological deodorizing apparatus described in Japanese Patent Application Laid-Open No. 4-363111, in which a horizontal horizontally long microbial growth section is provided in a horizontally long biological treatment tank, it is provided above the microbial growth section. In addition, there is a drawback that the gas to be treated is short-passed in the arrangement portion of the water sprinkling means and the liquid accumulation portion below and the deodorization efficiency is lowered.

【0013】上記における微生物着生材として土壌やピ
−ト等を用いる場合には、、廉価で単位容積当たりの表
面積も大きく脱臭効果も高いが、圧密化しやすいため圧
力損失が高くなりやすく、短期間で単位容積当たりの処
理ガス量が減少し、また長期間の使用により閉塞を起こ
す恐れもある。
When soil, peat or the like is used as the microbial engraftment material described above, it is inexpensive and has a large surface area per unit volume and a high deodorizing effect, but it tends to be compacted, resulting in high pressure loss and short-term. The amount of processing gas per unit volume decreases during that period, and there is a possibility that clogging may occur due to long-term use.

【0014】セラミックスや活性炭にあっては、上記の
土壌やピ−ト等と比較して圧力損失は低いが、微生物の
繁殖、夾雑物の混入等に伴って、圧力損失が増大しやす
いため、微生物の増殖管理も煩雑となり、また担体の価
格も高価である等の問題がある。
Although the pressure loss of ceramics and activated carbon is lower than that of the above-mentioned soil, peat, etc., the pressure loss is apt to increase due to the growth of microorganisms and the inclusion of foreign substances. There are problems that the control of the growth of microorganisms becomes complicated and the price of the carrier is expensive.

【0015】更に、上記微生物着生材を用いる場合に
は、いずれも重力や散水された水の影響で、微生物着生
部の上下方向に密度勾配が生じ易く、被処理ガスを水平
方向に流通させると、偏流を起こし易い問題もある。
Furthermore, in the case of using the above-mentioned microbial growth material, due to the influence of gravity or sprinkled water, a density gradient is likely to occur in the vertical direction of the microbial growth part, and the gas to be treated is circulated in the horizontal direction. If this is done, there is also a problem that a drift is likely to occur.

【0016】[0016]

【課題を解決するための手段】上記課題を解決するため
の本発明の要旨は、微生物着生部を内設した生物処理槽
により悪臭ガスを脱臭処理する生物脱臭装置において、
生物処理槽を水平横長の矩形体形状とし、その長手方向
の一端側に被処理ガスの供給口、他端側に処理ガスの排
出口を設け、生物処理槽の内部に、上端が生物処理槽の
上壁近傍に設けられた係着部材で上壁との間に間隙を生
じないよう係着され、下端を自由端として垂下された多
数の長尺繊維から成る微生物着生材を、被処理ガス流通
方向に交叉する断面の略全面に渡って設けた微生物着生
部と、微生物着生部に洗浄水を散布する散水手段と、底
部に微生物着生部の下部が浸漬するように水位が調節さ
れた液溜まり部を設けたことを特徴とする横型生物脱臭
装置である。
Means for Solving the Problems The gist of the present invention for solving the above-mentioned problems is to provide a biological deodorizing apparatus for deodorizing malodorous gas by a biological treatment tank having a microbial engraftment section,
The biological treatment tank is in the shape of a horizontally-long rectangular body, the gas to be treated inlet is provided at one end in the longitudinal direction, and the processing gas outlet is provided at the other end, with the upper end inside the biological treatment tank. The microbial engraftment material consisting of a large number of long fibers that are attached by an attachment member provided near the upper wall so as not to create a gap with the upper wall and hang down with the lower end as a free end is treated. The microbial-growth portion provided over substantially the entire cross-section that intersects in the gas flow direction, sprinkling means for spraying cleaning water to the microbial-growth portion, and the water level so that the bottom of the microbial-growth portion is immersed in the bottom part It is a horizontal biological deodorizing device characterized in that a regulated liquid reservoir is provided.

【0017】また、上記装置において、微生物着生部を
生物処理槽内の長手方向に複数段設けたことを特徴とす
る横型生物脱臭装置である。
Further, the above-mentioned apparatus is a horizontal type biological deodorizing apparatus characterized in that a plurality of stages for microbial growth are provided in the biological treatment tank in the longitudinal direction.

【0018】上記構成の横型生物脱臭装置により、生物
脱臭装置の設置面積や高さをできるだけ狭く、且つ低く
でき、また圧力損失も極めて低いため微生物着生部の段
数を任意に増加でき、微生物着生部に密度勾配を生じな
いため、偏流が発生せず脱臭効率の向上が図られる。
With the horizontal biological deodorizing device having the above-mentioned structure, the installation area and height of the biological deodorizing device can be made as narrow as possible and can be made as low as possible, and since the pressure loss is extremely low, the number of stages of the microbial growth part can be arbitrarily increased, and the microbial growth can be performed. Since there is no density gradient in the raw part, uneven flow does not occur and deodorization efficiency is improved.

【0019】また被処理ガスがショ−トパスして脱臭効
率が低くなることもなく、更に、微生物着生部を複数設
けた装置にあっては、夫々の微生物着生部毎に適正な散
水量を設定することによって、脱臭効率の向上が図れ、
また夫々の微生物着生部の散水洗浄において、洗浄後の
排水による相互の微生物着生部間での影響がないため、
微生物の棲息環境を良好に保つことができる。
Further, the gas to be treated does not short-pass and the deodorizing efficiency does not decrease. Further, in an apparatus provided with a plurality of microbial growth parts, an appropriate amount of water is sprinkled for each microbial growth part. By setting, the deodorization efficiency can be improved,
Also, in sprinkling and washing of each microbial growth part, there is no influence between the microbial growth parts due to the waste water after washing,
It is possible to maintain a good habitat for microorganisms.

【0020】[0020]

【発明の実施の形態】次に、本発明の実施の形態を図面
に基づいて説明する。図1は本発明の一実施の形態であ
る生物脱臭装置の一部切欠の概略側面図、図2は図1の
A−A視の縦断面図、図3は複数の微生物着生部を設け
た一部切欠の概略側面図、図4は他の実施の形態の一部
切欠の概略側面図であり、夫々相当する部材については
同一の符番を用いた。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Next, embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a schematic side view of a partial cutout of a biological deodorizing apparatus according to an embodiment of the present invention, FIG. 2 is a vertical sectional view taken along line AA of FIG. 1, and FIG. FIG. 4 is a schematic side view of a partial cutout, and FIG. 4 is a schematic side view of a partial cutout according to another embodiment. The same reference numerals are used for corresponding members.

【0021】1は水平横長の矩形体形状に形成し、その
長手方向の一端側に被処理ガスの供給口5、他端側に処
理ガスの排出口6を設けており、被処理ガスが長手方向
に流通するように構成された生物処理槽である。
Reference numeral 1 is formed in a horizontally long rectangular shape, and one end side in the longitudinal direction thereof is provided with a processing gas supply port 5 and the other end side is provided with a processing gas discharge port 6. The biological treatment tank is configured to flow in the direction.

【0022】上記生物処理槽1の内部には、上端が生物
処理槽の上壁近傍に設けられた係着部材11で上壁との
間に間隙を生じないよう係着され、下端を自由端として
垂下された多数の長尺繊維から成る微生物着生材10を
被処理ガス流通方向に交叉する断面の略全面に渡って設
けた微生物着生部2と、微生物着生部2の上部に洗浄水
を散布する散水手段3と、底部に微生物着生材10の下
部が浸漬するように水位が調節された液溜まり部4が設
けられている。
Inside the biological treatment tank 1, the upper end is fastened by a fastening member 11 provided in the vicinity of the upper wall of the biological treatment tank so that no gap is formed between the upper wall and the free end. A microbial growth part 2 in which a microbial growth material 10 composed of a large number of long fibers hanging down as a whole is provided over substantially the entire cross section crossing in the flow direction of the gas to be treated, and the upper part of the microbial growth part 2 is washed. A water sprinkling means 3 for spraying water and a liquid reservoir 4 in which the water level is adjusted so that the lower part of the microbial growth material 10 is immersed in the bottom part are provided.

【0023】尚、微生物着生材10としては、微生物の
良好な着生繁殖や、圧力損失及び気液接触効率等の観点
から、実公平6−47550号に記載された、表面積の
増大と微生物の流下損失防止が図れるポリプロピレンや
ビニロン等の合成繊維糸をル−プ状に形成して多数集束
した長尺の繊維束から成るのが好ましく、更に、繊維束
は微生物が着生しやすい合成繊維細糸を多数集束した束
糸と、型崩れ防止のための補強用の合成繊維太糸とを、
各々ル−プ状に形成して多数集束し長尺紐状とするのが
好ましい。
From the viewpoint of good vegetative growth of microorganisms, pressure loss, gas-liquid contact efficiency, etc., the microbial epiphytic material 10 is described in Japanese Utility Model Publication No. It is preferable that a long fiber bundle is formed by forming a large number of synthetic fiber yarns, such as polypropylene or vinylon, in a loop shape capable of preventing run-down loss, and further, the fiber bundle is a synthetic fiber in which microorganisms easily grow. A bundle of a large number of thin yarns, and a thick synthetic fiber yarn for reinforcement to prevent the shape from collapsing,
It is preferable that each is formed in a loop shape and is bundled in large numbers to form a long string.

【0024】また、上記微生物着生材10は多数の長尺
繊維の上端を金編みやスリット板又は水平棒等の係着部
材11に懸架して適宜に固着し、生物処理槽1の上壁と
微生物着生部2との間に間隙が生じないように設け、下
端を自由端とし垂下するが、微生物着生材10の下部が
液溜まり部4の液中に浸漬するように設けられる。
In addition, the above-mentioned microbial engraftment material 10 is appropriately fixed by suspending the upper ends of a large number of long fibers on an attachment member 11 such as a gold braid, a slit plate or a horizontal rod, and fixing it to the upper wall of the biological treatment tank 1. It is provided so that no gap is formed between the microbial growth part 2 and the microbial growth part 2, and the lower end thereof is hung down as a free end, but the lower part of the microbial growth material 10 is provided so as to be immersed in the liquid in the liquid pool part 4.

【0025】更に、上記散水手段3は夫々の微生物着生
部2にできるだけ均一に洗浄水が散布されるように、図
1に記載された装置のように、生物処理槽1の上壁近傍
で、微生物着生部2に沿って多数のスプレ−ノズルが水
平にほぼ等間隔で、配置されているのが好ましいが、図
4に記載された装置のように、上記スプレ−ノズルが上
下方向にも複数配置されるのも好ましい。
Further, the water sprinkling means 3 is provided in the vicinity of the upper wall of the biological treatment tank 1 in the same manner as in the device shown in FIG. It is preferable that a large number of spray nozzles are horizontally arranged at substantially equal intervals along the microbial growth portion 2, but as in the device shown in FIG. 4, the spray nozzles are arranged vertically. It is also preferable that a plurality of them are arranged.

【0026】生物処理槽1の底部に設けられる液溜まり
部4は、洗浄排水が合流されて一定量滞留された後、そ
のまま排水としてドレン排出管8から排出されるように
してもよく、また、微生物着生部2への散水手段3に循
環する洗浄水循環流路を設け洗浄排水を適宜に循環する
のも好ましい。
In the liquid reservoir 4 provided at the bottom of the biological treatment tank 1, the cleaning wastewater may be combined and retained for a certain amount, and then discharged as it is from the drain discharge pipe 8 as drainage. It is also preferable to provide a washing water circulation channel for circulating the water sprinkling means 3 to the microorganism-growth part 2 and appropriately circulate the washing waste water.

【0027】図3及び図4においては、微生物着生部2
が生物処理槽1内の長手方向に複数段設けられており、
水に溶解しやすく微生物により分解されやすい硫化水
素、アンモニア等が先に吸収分解され、有機硫黄化合物
等は、吸収されにくいため、多くは後段の微生物着生部
で吸収分解されるため、着生微生物が相違することもあ
り、液溜まり部4に滞留する洗浄後の洗浄排水が混合さ
れてもよいが、混合しないように微生物着生部2毎に区
画形成し、洗浄水として夫々の液溜まり部4に滞留する
洗浄排水を、夫々の微生物着生部2への散水手段3に循
環する洗浄水循環流路を設けるのも好ましい。
In FIGS. 3 and 4, the microbial growth part 2 is shown.
Are provided in multiple stages in the biological treatment tank 1 in the longitudinal direction,
Hydrogen sulfide, ammonia, etc., which are easily dissolved in water and easily decomposed by microorganisms, are absorbed and decomposed first, and organic sulfur compounds, etc., are difficult to be absorbed, and most of them are absorbed and decomposed in the microbial engraftment part in the latter stage, so that the settlement Since the microorganisms may be different, the cleaning waste water after cleaning which remains in the liquid pool 4 may be mixed, but each microorganism pool 2 is partitioned so as not to mix, and each liquid pool is used as cleaning water. It is also preferable to provide a washing water circulation flow path for circulating the washing waste water staying in the portion 4 to the water sprinkling means 3 to the respective microbial growth portions 2.

【0028】上記構成の生物脱臭装置で悪臭ガスを処理
する作用について以下記載する。し尿や下水処理場で発
生した悪臭成分を含有する被処理ガスを、図示しない吸
引ブロワで吸引し、給気管を経て被処理ガスの供給口5
から生物処理槽1へ供給する。
The operation of treating a malodorous gas with the biological deodorizing device having the above-mentioned structure will be described below. A gas to be treated containing a malodorous component generated in human waste or a sewage treatment plant is sucked by a suction blower (not shown), and the gas to be treated is supplied through an air supply pipe 5
To the biological treatment tank 1.

【0029】供給された悪臭ガスの被処理ガスは、微生
物着生部2の多数の長尺繊維から成る微生物着生材10
群の間隙を水平方向にクロスフロ−で流通する間に、悪
臭成分が微生物着生材10に保持された水分に吸収され
ると共に、着生微生物により生物学的に分解されて清浄
化される。清浄化された悪臭ガスは処理ガスとして処理
ガスの排出口6から図示しない排気管を経て大気中に放
出される。
The supplied odorous gas to be treated is a microbial-growth material 10 comprising a large number of long fibers of the microbial-growth section 2.
During the horizontal cross flow through the gaps between the groups, the malodorous components are absorbed by the water retained in the microbial epiphytic material 10 and biologically decomposed by the epiphytic microorganisms for cleaning. The cleaned offensive odor gas is discharged as a processing gas from the processing gas outlet 6 into the atmosphere through an exhaust pipe (not shown).

【0030】尚上記において、微生物着生部2の上端と
生物処理槽1の上壁との間に間隙がなく、また微生物着
生部2の下部が液溜まり部4に滞留する水中に浸漬され
ているため、水平に流通する被処理ガスがシ−トパスす
る恐れもなく、微生物着生部に密度勾配を生じないた
め、偏流が発生せず脱臭効率が低下する恐れもない。
In the above description, there is no gap between the upper end of the microbial growth part 2 and the upper wall of the biological treatment tank 1, and the lower part of the microbial growth part 2 is immersed in the water accumulated in the liquid pool part 4. Therefore, there is no fear that the gas to be horizontally circulated will be sheet-passed, and no density gradient will occur in the microbial engraftment portion, so that no deviated flow will occur and the deodorization efficiency will not decrease.

【0031】悪臭ガス中に含有する悪臭成分としては硫
化水素、メチルメルカプタン等の硫黄化合物やアンモニ
アが主であり、それらは、微生物により硫酸や硝酸等に
分解される。また硫酸等の酸性成分が生成することによ
り、微生物着生部のPHが低下する恐れがあるが、後記
の散水により微生物の生育に適したPH値に維持するこ
とができる。
The malodorous components contained in the malodorous gas are mainly hydrogen sulfide, sulfur compounds such as methyl mercaptan and ammonia, which are decomposed by microorganisms into sulfuric acid, nitric acid and the like. In addition, the production of acidic components such as sulfuric acid may lower the PH of the microbial-growth site, but watering as described below can maintain the PH value suitable for the growth of microorganisms.

【0032】運転初期における微生物着生部2への微生
物の着生は、し尿や下水などの生物学的処理水の散水の
みで行ってもよいが、微生物着生材10を活性汚泥に数
時間程度浸漬して用いることにより、更に速く定常状態
の脱臭効率を得ることができる。
The microorganisms can be settled on the microbial growth portion 2 at the initial stage of operation by only sprinkling biologically treated water such as human waste or sewage, but the microbial growth material 10 is placed on the activated sludge for several hours. By immersing it for a while, the deodorizing efficiency in the steady state can be obtained even faster.

【0033】微生物着生部2への散水は、図示しない給
水ポンプで洗浄水供給管7を経て散水手段3の散水ノズ
ルから、連続または間欠的に散布される。この散水によ
り、微生物の生育に必要な栄養の供給や湿潤状態が確保
され、微生物の増殖を促進し、また悪臭成分の分解によ
り生成する硫酸や過剰の微生物を洗浄除去することがで
き、好適PHの維持、微生物の過剰着生を防止すること
ができる。
The sprinkling of water on the microbial growth part 2 is continuously or intermittently sprinkled from a sprinkling nozzle of the sprinkling means 3 through a wash water supply pipe 7 by a water supply pump (not shown). By this watering, the supply of nutrients necessary for the growth of microorganisms and the moist state are secured, the growth of microorganisms is promoted, and the sulfuric acid and excess microorganisms produced by the decomposition of the malodorous components can be washed and removed. It is possible to maintain the above, and to prevent excessive settlement of microorganisms.

【0034】上記散水に使用される水としては、工業用
水、水道水等でもよいが、し尿や下水等の生物学的処理
水が、微生物や栄養素を適当に含有し、またアルカリ性
の成分も含有しているため、微生物増殖、好適PH維持
のためには好ましく、更に適宜に洗浄後の洗浄排水を用
いてもよい。
The water used for the sprinkling may be industrial water, tap water, etc., but biologically treated water such as human waste or sewage appropriately contains microorganisms and nutrients, and also contains alkaline components. Therefore, it is preferable for the growth of microorganisms and the maintenance of a suitable pH, and the washing waste water after washing may be used as appropriate.

【0035】尚、悪臭成分の微生物分解においては、P
H値が重要な因子となっており、悪臭成分の種類によっ
てその値も相違し、因みに、硫化水素にあっては、PH
4以下、メチルメルカプタン、硫化メチル等の有機硫黄
化合物にあっては、PH5〜6程度が至適なPH領域で
ある。
In the microbial decomposition of the malodorous component, P
The H value is an important factor, and its value also differs depending on the type of malodorous component.
For organic sulfur compounds such as methyl mercaptan and methyl sulfide having a pH of 4 or less, a PH range of 5 to 6 is the optimum PH range.

【0036】また、微生物を着生した微生物着生部2で
は、水に溶解しやすく微生物により分解されやすい硫化
水素、アンモニア等が先に吸収分解され、有機硫黄化合
物等は、吸収分解が遅れるため、上記の悪臭ガスが複数
の微生物着生部2を順次流通する処理においては、前段
の微生物着生部2ほど硫化水素、アンモニア等が主に吸
収分解され、その分解生成物である硫酸や硝酸等の酸性
成分が蓄積し、PH値が極めて低くなり、有機硫黄化合
物は後段の微生物着生部2で除去されることになる。
Further, in the microbial growth part 2 on which the microorganisms have settled, hydrogen sulfide, ammonia, etc., which are easily dissolved in water and easily decomposed by the microorganisms, are absorbed and decomposed first, and the organic sulfur compounds, etc. are delayed in absorption and decomposition. In the process in which the malodorous gas sequentially flows through the plurality of microbial-growth parts 2, hydrogen sulfide, ammonia and the like are mainly absorbed and decomposed in the microbial-growth part 2 in the preceding stage, and the decomposition products thereof are sulfuric acid and nitric acid. Acidic components such as, for example, accumulate, the PH value becomes extremely low, and the organic sulfur compound is removed by the microbial growth part 2 in the subsequent stage.

【0037】本発明の複数の微生物着生部2を設けた装
置においては、夫々の微生物着生部2の上方に設けられ
た散水手段3で 個別に散水し、洗浄後の排水は他の微
生物着生部2を経ないようにされているため、前段の低
PH洗浄排水により後段の微生物着生部2に担持された
微生物に影響を与えることがなく、常に夫々の微生物着
生部2の状態を、微生物が棲息するに好適な環境に維持
することができる。
In the apparatus provided with a plurality of microbial growth parts 2 of the present invention, water is sprayed individually by the water spraying means 3 provided above each microbial growth part 2, and the waste water after washing is used for other microorganisms. Since it does not pass through the settlement section 2, it does not affect the microorganisms carried in the microorganisms settlement section 2 of the latter stage by the low-pH washing drainage of the preceding stage, and the microbial settlements of the respective microorganisms settlement section 2 are always maintained. The condition can be maintained in an environment suitable for habitation of microorganisms.

【0038】尚、微生物着生部2の散水洗浄後の洗浄排
水は、生物処理槽1の液溜まり部4で合流されて一定量
滞留された後、そのまま排水としてドレン排出管8から
排出してもよく、また微生物着生部2毎に区画して一定
量滞留した洗浄排水を、夫々の洗浄水として循環使用す
ると共に、一部を合流した後洗浄排水として排出するこ
とも好ましい。
The cleaning wastewater after the sprinkling and cleaning of the microorganism-adhering portion 2 is merged in the liquid pool portion 4 of the biological treatment tank 1 and retained for a certain amount, and then discharged as drainage from the drain discharge pipe 8 as it is. Alternatively, it is also preferable that the cleaning waste water, which is divided for each microbial growth portion 2 and stays in a certain amount, is circulated and used as each cleaning water, and a part of the cleaning waste water is joined and then discharged as the cleaning waste water.

【0039】更に、生物処理槽1での悪臭ガスの流通速
度は、0.1〜0.5m/secとするのが好ましく、
0.1m/sec以下の流通速度では、ガス流の偏流が
生じやすく、また0.5m/sec以上の流通速度では
微生物着生部2内での圧力損失の増大が生じやすい。
Further, the flow rate of the malodorous gas in the biological treatment tank 1 is preferably 0.1 to 0.5 m / sec,
At a flow rate of 0.1 m / sec or less, a nonuniform flow of the gas flow is likely to occur, and at a flow rate of 0.5 m / sec or more, an increase in pressure loss in the microbial growth part 2 is likely to occur.

【0040】[0040]

【発明の効果】本発明は、生物脱臭装置の設置面積や高
さをできるだけ狭く且つ低くでき、また圧力損失が極め
て低いため、微生物着生部の段数を任意に増加でき、脱
臭効率の向上を図ることができ、また微生物着生部に密
度勾配を生じないため、偏流が発生することがないと共
に、被処理ガスがショ−トパスする恐れもないため脱臭
効率が低くなることもなく、更に、夫々の微生物着生部
の散水洗浄において、洗浄後の排水による相互の微生物
着生部間での影響がないため、微生物の棲息環境を良好
に保つことができる。
INDUSTRIAL APPLICABILITY According to the present invention, since the installation area and height of the biological deodorizing device can be made as narrow and low as possible, and the pressure loss is extremely low, the number of stages of the microbial engraftment portion can be arbitrarily increased and the deodorizing efficiency can be improved. It is possible to achieve, and because a density gradient does not occur in the microbial engraftment portion, a non-uniform flow does not occur, and the deodorizing efficiency does not decrease because the gas to be treated is not likely to short-pass, and further, In sprinkling and washing the respective microbial-growth sites with water, since there is no influence between the microbial-growth parts due to the waste water after the washing, the habitat environment of the microorganisms can be kept good.

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

【図1】本発明の一実施の形態である生物脱臭装置の一
部切欠の概略側面図
FIG. 1 is a schematic side view of a partial cutout of a biological deodorizing apparatus according to an embodiment of the present invention.

【図2】図1のA−A視の縦断面図FIG. 2 is a vertical sectional view taken along line AA of FIG.

【図3】複数の微生物着生部を設けた一部切欠の概略側
面図
FIG. 3 is a schematic side view of a partial cutout provided with a plurality of microbial settlements.

【図4】他の実施の形態の一部切欠の概略側面図FIG. 4 is a schematic side view of a partial cutout according to another embodiment.

【符号の説明】[Explanation of symbols]

1:生物処理槽 2:微生物着生部 3:散水手段 4:液溜まり部 5:被処理ガスの供給口 6:処理ガスの排出口 7:洗浄水の供給管 8:ドレン排出管 10:微生物着生材 11:係着部材 1: Biological treatment tank 2: Microorganism engraftment part 3: Sprinkling means 4: Liquid reservoir part 5: Supply port for gas to be treated 6: Discharge port for process gas 7: Supply pipe for washing water 8: Drain discharge pipe 10: Microorganism Epiphytic material 11: Engagement member

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】微生物着生部を内設した生物処理槽により
悪臭ガスを脱臭処理する生物脱臭装置において、生物処
理槽を水平横長の矩形体形状とし、その長手方向の一端
側に被処理ガスの供給口、他端側に処理ガスの排出口を
設け、生物処理槽の内部に、上端が生物処理槽の上壁近
傍に設けられた係着部材で上壁との間に間隙を生じない
よう係着され、下端を自由端として垂下された多数の長
尺繊維から成る微生物着生材を、被処理ガス流通方向に
交叉する断面の略全面に渡って設けた微生物着生部と、
微生物着生部に洗浄水を散布する散水手段と、底部に微
生物着生部の下部が浸漬するように水位が調節された液
溜まり部を設けたことを特徴とする横型生物脱臭装置。
1. A biological deodorizing apparatus for deodorizing malodorous gas in a biological treatment tank having a microorganism-growth part internally provided, wherein the biological treatment tank has a horizontally long rectangular body shape, and the gas to be treated is provided on one end side in the longitudinal direction thereof. Of the feed gas and a discharge port for the treatment gas at the other end, and the upper end is provided inside the biological treatment tank near the upper wall of the biological treatment tank so that no gap is formed between the upper and the upper wall. Thus, a microbial growth material comprising a large number of long fibers suspended with the lower end as a free end, a microbial growth portion provided over substantially the entire cross-section intersecting the direction of gas flow to be treated,
A horizontal biological deodorizing device comprising: a sprinkling means for spraying washing water to the microorganism-growth part, and a liquid pool part having a water level adjusted so that the lower part of the microorganism-growth part is immersed in the bottom part.
【請求項2】微生物着生部を生物処理槽内の長手方向に
複数段設けたことを特徴とする請求項1記載の横型生物
脱臭装置。
2. The horizontal biological deodorizer according to claim 1, wherein a plurality of stages for microbial settlement are provided in the biological treatment tank in the longitudinal direction.
JP8159274A 1996-05-31 1996-05-31 Horizontal biological deodorizing device Pending JPH09313871A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8159274A JPH09313871A (en) 1996-05-31 1996-05-31 Horizontal biological deodorizing device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8159274A JPH09313871A (en) 1996-05-31 1996-05-31 Horizontal biological deodorizing device

Publications (1)

Publication Number Publication Date
JPH09313871A true JPH09313871A (en) 1997-12-09

Family

ID=15690207

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8159274A Pending JPH09313871A (en) 1996-05-31 1996-05-31 Horizontal biological deodorizing device

Country Status (1)

Country Link
JP (1) JPH09313871A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20000006651A (en) * 1999-09-17 2000-02-07 임재신 Horizontal biofilter for removing odor compounds and VOCs

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20000006651A (en) * 1999-09-17 2000-02-07 임재신 Horizontal biofilter for removing odor compounds and VOCs

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