JPH01315317A - Deodorizing device for gas - Google Patents

Deodorizing device for gas

Info

Publication number
JPH01315317A
JPH01315317A JP63146998A JP14699888A JPH01315317A JP H01315317 A JPH01315317 A JP H01315317A JP 63146998 A JP63146998 A JP 63146998A JP 14699888 A JP14699888 A JP 14699888A JP H01315317 A JPH01315317 A JP H01315317A
Authority
JP
Japan
Prior art keywords
packed bed
gas
packed
malodorous components
microorganisms
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
JP63146998A
Other languages
Japanese (ja)
Inventor
Hirohisa Yamada
山田 尋久
Shin Nakashio
中塩 伸
Yoshinari Fujisawa
能成 藤沢
Yasunori Tanji
保典 丹治
Eiichi Sugiura
鋭一 杉浦
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan 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 NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP63146998A priority Critical patent/JPH01315317A/en
Publication of JPH01315317A publication Critical patent/JPH01315317A/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

Abstract

PURPOSE:To eliminate clogging of packed beds of a gas deodorizing device by constituting the device of a lower stage packed bed section for deodorization by a physicochemical method and an upper stage packed bed section for deodorization by a biological method by spraying washing water, and regulating grain size of the carrier in the lower stage deodorizing section to a larger grain size than that in the upper deodorizing section. CONSTITUTION:A packed bed 15 packed with many carriers comprising ceramic granules, etc.,is formed to a two-layered structure, and carriers having larger grain size than carriers in the upper stage packed bed 15b are packed in the lower stage packed bed 15a, and carriers having an intermediate grain size are packed in the upper stage packed bed 15b. Washing water from a water spray nozzle pipe 16 washes off decomposed product of malodorous components produced by the effect of microorganisms sticking to the surface of the carriers in the packed bed 15b, and becomes acidic. Gas 10 to be treated from an opening port 13 is allowed to contact with the acidic washing water in the packed bed 15a and neutralizes and removes basic malodorous components in the gas 10. Then, residual malodorous components are decomposed by microorganisms in the packed bed 15b a discharged from a discharging port 14. Since the grain size of the carrier in the lower stage packed bed is larger than that in the upper packed bed, clogging of the packed bed 15a due to sludge generated in the packed bed 15b is reduced.

Description

【発明の詳細な説明】 [産業上の利用分野コ 本発明は、微生物による生物学的処理法と薬液洗浄によ
る物理化学的処理法を組合せたガスの脱臭装置に関し、
畜産農業、飼料・肥料製造工場、化学工場、下水処理場
等あらゆる分野で発生する排気ガスの脱臭処理に利用す
ることができるものである。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a gas deodorizing device that combines a biological treatment method using microorganisms and a physicochemical treatment method using chemical cleaning.
It can be used to deodorize exhaust gas generated in all fields such as livestock farming, feed and fertilizer manufacturing plants, chemical plants, and sewage treatment plants.

[従来の技術] 気相中に含まれる悪臭成分を除去する方法としては、燃
焼法、薬液洗浄法、吸着法等の物理化学的方法と、土壌
脱臭法、活性汚泥法等の生物学的方法とが知られている
が、近年二次公害がなく多様なガスを同時処理でき、か
つ処理コストの低置な生物学的方法が注目を浴びている
[Prior art] Methods for removing malodorous components contained in the gas phase include physicochemical methods such as combustion methods, chemical cleaning methods, and adsorption methods, and biological methods such as soil deodorization methods and activated sludge methods. However, in recent years, biological methods that do not cause secondary pollution, can simultaneously process a variety of gases, and have low processing costs have been attracting attention.

生物学的方法の一例を第2図により説明すると、図にお
いて、1は脱臭塔であり、その内部には図示しない充填
物(坦体)を積層した充填層2があり、それらの充填物
の表面には微生物が付着せしめられている。3は定期的
に充填層2に散水しこれを洗浄するための散水ノズル管
である。4は脱臭塔1の下底部に設けられた洗浄水槽で
、充填層2を通して落下する水を貯留し循環使用するよ
うになっている。5は必要時洗浄水槽4に供給管6によ
りアルカリ剤を供給するためのアルカリ剤槽で、洗浄水
のpH値を微生物の活性を維持する範囲(通常pH6〜
8)に調整するために使用される。7は洗浄水の塩濃度
を微生物の活性を阻害しない程度に調整する補給水の供
給管である。図中、8は放流水管である。
An example of the biological method will be explained with reference to FIG. 2. In the figure, 1 is a deodorizing tower, inside which there is a packed bed 2 in which packing materials (carriers) (not shown) are laminated, and the Microorganisms are attached to the surface. 3 is a water spray nozzle pipe for periodically spraying water on the packed bed 2 to clean it. Reference numeral 4 denotes a washing water tank provided at the bottom of the deodorizing tower 1, in which water falling through the packed bed 2 is stored and circulated. Reference numeral 5 denotes an alkaline agent tank for supplying an alkaline agent to the cleaning water tank 4 through a supply pipe 6 when necessary, and the pH value of the cleaning water is kept within a range that maintains the activity of microorganisms (usually pH 6 to 6).
8). Reference numeral 7 denotes a make-up water supply pipe for adjusting the salt concentration of the washing water to an extent that does not inhibit the activity of microorganisms. In the figure, 8 is a discharge water pipe.

次にその動作を説明する。Next, its operation will be explained.

被処理ガス10は脱臭塔1の下部より送入され、充填層
2を上昇通過する間に充填物の表面に付着した微生物と
接触させ、微生物によって被処理ガス10に含まれてい
る悪臭成分を分解する。この分解の結果発生する生成物
は定期的に散水ノズル管3より洗浄水を充填層2に散水
することによって充填物の表面から洗い流され、また、
散水により微生物に対する水分補給がなされる。この場
合、洗浄水は充填層2を通して下方の洗浄水槽4に落下
貯留し、これを循環使用するようになっているので、繰
り返し使用するうちに洗浄水のpH値が次第に低下して
微生物の活性を阻害する。そこで、これを防止するため
アルカリ剤rとして例えば苛性ソーダをアルカリ剤槽5
から時々供給して洗浄水を中和する。また、苛性ソーダ
の供給により洗浄水中の塩濃度が増加し、このため微生
物の活性を阻害するので、所定の塩濃度以下に保持する
ため洗浄水の一部を放流水管8により放流するとともに
、補給水波給管7より新水を補給する。
The gas to be treated 10 is fed from the lower part of the deodorizing tower 1, and while rising and passing through the packed bed 2, it is brought into contact with microorganisms attached to the surface of the packed material, and the malodorous components contained in the gas to be treated 10 are removed by the microorganisms. Disassemble. The products generated as a result of this decomposition are washed away from the surface of the packing by periodically sprinkling cleaning water onto the packing bed 2 from the water spray nozzle pipe 3, and
Watering provides hydration to microorganisms. In this case, the cleaning water falls through the packed bed 2 and is stored in the cleaning water tank 4 below and is used for circulation.As the cleaning water is used repeatedly, the pH value of the cleaning water gradually decreases and the microorganisms become active. inhibit. Therefore, in order to prevent this, for example, caustic soda is added to the alkaline agent tank 5 as an alkaline agent r.
Supply water from time to time to neutralize the wash water. In addition, the salt concentration in the wash water increases due to the supply of caustic soda, which inhibits the activity of microorganisms. Therefore, in order to maintain the salt concentration below a predetermined level, a portion of the wash water is discharged through the discharge water pipe 8, and a make-up water wave is Replenish fresh water from supply pipe 7.

被処理ガスlOは充填層2を通すことにより、上記のよ
うに含有する悪臭成分を除去され、無臭のガス10aと
なって脱臭塔1の上部より大気中に放出される。
By passing the gas to be treated 10 through the packed bed 2, the malodorous components contained therein are removed as described above, and the odorless gas 10a is released into the atmosphere from the upper part of the deodorizing tower 1.

[発明が解決しようとする課題] 従来の悪臭ガスの脱臭装置は、以上のように充填層2に
積層された充填物の表面に微生物を付着させ、この微生
物と被処理ガス10とを接触させることにより、含有す
る悪臭成分を微生物により分解させるものであるから、
微生物の利用上の自由度は高まる。つまり、悪臭成分が
硫化水素のような硫黄系であろうとアンモニアのような
窒素含有物質系であろうとその悪臭成分を分解するよう
な性質を持つ微生物が発生増殖する。したがって、微生
物学的脱臭はとくに処理コストの低廉に大きく寄与する
。しかしながら、従来装置においては次のような点でな
お問題があった。
[Problems to be Solved by the Invention] The conventional deodorizing device for malodorous gas attaches microorganisms to the surface of the filling layered in the filling layer 2 as described above, and brings the microorganisms into contact with the gas to be treated 10. As a result, the malodorous components contained are decomposed by microorganisms.
The degree of freedom in using microorganisms will increase. In other words, microorganisms that have the property of decomposing malodorous components develop and proliferate, regardless of whether the malodorous components are sulfur-based such as hydrogen sulfide or nitrogen-containing substances such as ammonia. Therefore, microbiological deodorization particularly contributes significantly to lower processing costs. However, the conventional device still has the following problems.

(1)大量の悪臭成分の除去を必要とする場合、微生物
の悪臭成分の分解速度には制限があるため、脱臭装置が
大型複雑になり用地の確保等の点で困難な問題が生じる
。そのため用途も制約されやすい。
(1) When it is necessary to remove a large amount of malodorous components, there is a limit to the decomposition rate of malodorous components by microorganisms, so the deodorizing equipment becomes large and complex, creating difficult problems in terms of securing land, etc. Therefore, the usage is also likely to be restricted.

(2)悪臭成分の濃度が高くなると微生物の活性が阻害
されるため、高濃度悪臭の除去を行う場合は他の脱臭装
置との併設が必要となり、大型複雑化する。悪臭成分の
濃度変動が大きい場合、微生物の悪臭成分分解速度の追
随が遅いため、他の脱臭装置との併設が必要となり、上
記(2)と同様の問題が生じる。
(2) When the concentration of malodorous components increases, the activity of microorganisms is inhibited, so when removing high-concentration malodors, it is necessary to install other deodorizing equipment, which increases the size and complexity. If the concentration of the malodorous component varies greatly, the decomposition rate of the malodorous component by microorganisms will be slow to follow, making it necessary to install another deodorizing device, resulting in the same problem as in (2) above.

(3)上記(1)、 (2)と共に、生物学的処理方法
の特徴である処理コストの低廉さというメリットを減少
させる。
(3) Along with (1) and (2) above, it reduces the advantage of low processing costs, which is a feature of biological treatment methods.

(4)悪臭成分を微生物によって分解質化させた時に発
生する汚泥により充填層を目づまりさせやすい。
(4) The sludge generated when malodorous components are decomposed by microorganisms tends to clog the packed bed.

本発明は、上記のような従来法の問題点を解消するため
になされたもので、小型簡潔な構成により、高効率にし
かも充填層の目づまりをなくしてガスの脱臭処理ができ
る脱臭装置を提供することを目的とするものである。
The present invention has been made in order to solve the problems of the conventional methods as described above, and provides a deodorizing device that has a small and simple configuration and can deodorize gas with high efficiency and eliminates clogging of the packed bed. The purpose is to

[課題を解決するための手段] 本発明に係るガスの脱臭装置は脱臭塔内の充填層を下方
に位置する物理化学的方法により悪臭成分を除去する機
能を有する下段の充填層部と、該充填層部より上方に位
置し、洗浄水が散水され、生物学的方法により悪臭成分
を除去する機能を有する上段の充填層部とで形成し、こ
れら充填層部の坦体の粒径を上段の充填層部よりも下段
の充填層部のほうを大きくするようにしたものである。
[Means for Solving the Problems] A gas deodorizing device according to the present invention includes a packed bed in a deodorizing tower, a lower packed bed portion located below and having a function of removing malodorous components by a physicochemical method, and The upper packed layer is located above the packed bed and is sprayed with washing water, and has the function of removing malodorous components using a biological method. The lower filled layer portion is made larger than the filled layer portion of the lower layer.

[作用] 本発明においては、脱臭塔の充填層を下方に位置する物
理化学的方法により悪臭成分を除去する機能を有する下
段の充填層部と該充填層部より上方に位置する生物学的
方法により悪臭成分を除去する機能を有する上段の充填
層部とで形成したから、脱臭塔の下部に導入された被処
理ガスは下段及び上段の充填層部を順に経由して、大気
中に放出されるが、まず上段の充填層部においてガス中
の悪臭成分の微生物による分解が行われる。次に、上段
の充填層を洗浄水で洗浄すると、この洗浄水中には上段
の充填層部で生成された酸を含んでおり、その酸性の洗
浄水は下段の充填層部の洗浄に使用される。下段の充填
層部においては、酸性の洗浄水と被処理ガスとが気液接
触するので、そのガス中のアンモニア、メチルアミン、
ジメチルアミン、トリメチルアミンなどの塩基性悪臭成
分が中和して除去され、酸性の洗浄水も中性となって洗
浄槽内に落下する。
[Function] In the present invention, a lower packed bed section having the function of removing malodorous components by a physicochemical method located below the packed bed of the deodorizing tower and a biological method located above the packed bed section are provided. Since the deodorizing tower is formed with an upper packed bed section that has the function of removing malodorous components, the gas to be treated that is introduced into the lower part of the deodorizing tower passes through the lower and upper packed bed sections in order and is released into the atmosphere. First, the malodorous components in the gas are decomposed by microorganisms in the upper packed bed section. Next, when the upper packed bed is washed with washing water, this washing water contains the acid generated in the upper packed bed, and the acidic washing water is used to wash the lower packed bed. Ru. In the lower packed bed section, the acidic cleaning water and the gas to be treated come into gas-liquid contact, so that ammonia, methylamine,
Basic malodorous components such as dimethylamine and trimethylamine are neutralized and removed, and the acidic cleaning water becomes neutral and falls into the cleaning tank.

このように、下段の充填層部において被処理ガス中の塩
基性悪臭成分の大部分が中和して除去されるため、上段
の充填層部には負荷の少ないしかも負荷変動の少ない被
処理ガスが送入されることになる。従って、上段の充填
層部にかかる負荷が量的質的にも軽減するため、上段の
充填層において微生物の活性、追随性を阻害されること
なしに被処理ガス中に残存する悪臭成分を迅速に分解処
理することができる。
In this way, most of the basic malodorous components in the gas to be treated are neutralized and removed in the lower packed bed, so the gas to be treated with less load and less load fluctuation is transferred to the upper packed bed. will be sent. Therefore, the load on the upper packed bed is reduced both quantitatively and qualitatively, so the malodorous components remaining in the gas to be treated are quickly removed without inhibiting the activity and followability of microorganisms in the upper packed bed. It can be disassembled and processed.

また、これら充填層部の坦体の粒径を上段の充填層部よ
りも下段の充填層部へいくに従い次第に大きくしてい゛
るから、空間率即ち隙間の断面積が大きくなって上段の
充填層部において微生物によって悪臭成分を分解質化さ
せた時に発生する汚泥による下段の充填層部の目詰りも
減少する。
In addition, since the grain size of the carrier in these packed bed parts is gradually increased from the upper packed bed part to the lower packed bed part, the void ratio, that is, the cross-sectional area of the gap increases, and the upper part of the packed bed becomes larger. Clogging of the lower packed bed section due to sludge generated when malodorous components are decomposed by microorganisms in the bed section is also reduced.

[実施例] 以下、本発明を図に示す実施例について詳述する。[Example] DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described in detail below with reference to embodiments shown in the drawings.

第1図は本発明の実施例を示す概略構成図である。FIG. 1 is a schematic configuration diagram showing an embodiment of the present invention.

図において、11は円筒状の脱臭塔で、下部には洗浄水
槽12が設けられている。L2aは洗浄水槽12に付設
された撹拌槽である。13は洗浄水槽12に開口する被
処理ガスIOの送入口、14は脱臭塔11の頂部に設け
られた処理ガスの排出口である。15は例えばセラミッ
ク系の粒状物(以下坦体という)が多数充填されている
充填層である。この充填層15は下段及び上段の充填層
部15a、15bを有する二層構造に形成されている。
In the figure, 11 is a cylindrical deodorizing tower, and a washing water tank 12 is provided at the bottom. L2a is a stirring tank attached to the washing water tank 12. Reference numeral 13 is an inlet for the gas to be treated IO which opens into the cleaning water tank 12, and reference numeral 14 is an outlet for the treated gas provided at the top of the deodorizing tower 11. Reference numeral 15 denotes a filling layer filled with a large number of ceramic particles (hereinafter referred to as carriers), for example. This filling layer 15 is formed into a two-layer structure having lower and upper filling layer portions 15a and 15b.

下段の充填層部15a内には粒径が20〜30+aff
l程度となるような比表面積100rtf/n+3以上
、空間率70%以上の大きな粒径の坦体が充填されてお
り、上段の充填層部15b内には粒径が10〜20mm
程度となるような比表面積150rr?/m3以上、空
間率50%以上の中位の粒径の担体が充填されている。
The particle size is 20 to 30+af in the lower packed bed part 15a.
A large particle size carrier having a specific surface area of 100rtf/n+3 or more and a void ratio of 70% or more is filled so that the particle diameter is about 10 mm to 20 mm in the upper packed layer section 15b.
A specific surface area of 150rr? /m3 or more and a medium particle size carrier with a void ratio of 50% or more is filled.

16は上段の充填層部15bに散水しこれを洗浄するた
めの散水ノズル管である。
Reference numeral 16 denotes a water spray nozzle pipe for spraying water on the upper packed bed portion 15b to clean it.

なお、下段及び上段充填層部15a、 15bに充填さ
れる坦体は表面に気孔を有し、保水性が高いものであれ
ば、材質はセラミック以外の高分子、繊維活性炭のよう
なものであってもよい。また、形状も粒状、格子状、ラ
シヒリング、円柱状、砕石状などを問わない。
The carrier filled in the lower and upper packed layer parts 15a and 15b may be made of a material other than ceramic, such as a polymer or fiber activated carbon, as long as it has pores on its surface and has high water retention. You can. Further, the shape may be granular, lattice, Raschig ring, columnar, crushed stone, or the like.

かかる坦体に付着させられる微生物としては従来使用し
ていた微生物と同等の酸化分解機能を有するものであれ
はよいが、より能率的な処理をするため、例えばチオバ
チルス属に属する細菌、チオバチルス・チオパルスを利
用することが望ましい。
The microorganisms that can be attached to such carriers may be those that have the same oxidative decomposition function as the microorganisms that have been used conventionally, but for more efficient processing, for example, bacteria belonging to the genus Thiobacillus, Thiobacillus thioparus. It is desirable to use

次に、上記のように構成した本発明の詳細な説明する。Next, the present invention configured as described above will be explained in detail.

まず、洗浄水槽12及び撹拌層12a内に中性水である
洗浄水を満たしておき、ついで、送入口13がら被処理
ガスIOを送入する。このとき、送入された被処理ガス
lOは下段及び上段の充填層部15a。
First, the cleaning water tank 12 and the stirring layer 12a are filled with cleaning water, which is neutral water, and then the gas to be treated IO is introduced through the inlet 13. At this time, the supplied gas to be treated 10 is supplied to the lower and upper packed layer portions 15a.

15bを経由して排出口14から大気中に放出されるが
、まず、上段の充填層部15bにおいてガス中の悪臭成
分の微生物の分解が行われる。この場合の生成分は下記
に代表される。
The gas is discharged into the atmosphere from the exhaust port 14 via the gas 15b, and first, the malodorous components in the gas are decomposed by microorganisms in the upper packed bed section 15b. The generated components in this case are represented by the following:

NH−+N  SH0 H2S−H2SO4,S CHSH−+HSo  、H2O,Co2(CH)  
5−4HSo  、H2O,CO2次に、上記の生成物
は、微生物の活性を保持するために定期的に散水ノズル
管16より散水される洗浄水によって上段の充填層部1
5bより洗い流される。そのため、上段の充填層部15
bを流下する洗浄水は微生物により分解生成された酸を
含むため、この酸性の洗浄水が下方に位置する下段の充
填層部15a上に落下散水してこれを洗浄することとな
る。その酸性洗浄水は下段の充填層部15aの洗浄に使
用される。下段の充填層部15aでは酸性洗浄水と被処
理ガスlOとが気液接触するので、被処理ガスlO中に
含まれている塩基性悪臭成分、例えばアンモニア、メチ
ルアミン、ジメチルアミン、トリメチルアミンなどが中
和され、被処理ガスlO中から除去される。この結果、
上段の充填層部15bには下段の充填層部15aで塩基
性悪臭成分の大部分が除去された被処理ガス10が到達
するので、上段の充填層部15bの負荷を大巾に軽減す
ることができる。
NH-+N SH0 H2S-H2SO4, S CHSH-+HSo, H2O, Co2(CH)
5-4 HSo, H2O, CO2 Next, the above-mentioned products are washed into the upper packed bed section 1 by washing water periodically sprinkled from the water spray nozzle pipe 16 to maintain the activity of microorganisms.
It is washed away from 5b. Therefore, the upper filled layer part 15
Since the washing water flowing down b contains acid decomposed and produced by microorganisms, this acidic washing water is sprayed onto the lower packed bed section 15a located below to wash it. The acidic cleaning water is used for cleaning the lower packed bed section 15a. In the lower packed bed section 15a, the acidic cleaning water and the gas to be treated 1O come into gas-liquid contact, so that basic malodorous components such as ammonia, methylamine, dimethylamine, trimethylamine, etc. contained in the gas to be treated 1O are removed. It is neutralized and removed from the gas to be treated. As a result,
Since the gas to be treated 10 from which most of the basic malodorous components have been removed in the lower packed bed section 15a reaches the upper packed bed section 15b, the load on the upper packed bed section 15b can be greatly reduced. I can do it.

また、下段及び上段の充填層部15a、lSb内に充填
されている坦体の粒径を上段の充填層部15bよりも下
段の充填層部15aのほうを大きくし、空間率が大きく
即ち隙間の断面積を大きくとるようにしているから、上
段の充填層部15bにおいて微生物によって悪臭成分を
分解質化させた時に発生する汚泥による下段の充填層部
15aの目詰まりも減少させることができる。更に、下
段の充填層部15aの坦体は上段の充填層部15bの坦
体に比し、通気抵抗に対して比表面積が大であるから、
上記気液接触時における物理化学的反応が効率良く行わ
れることとなる。
In addition, the particle size of the carriers filled in the lower and upper packed layer parts 15a and 1Sb is made larger in the lower packed layer part 15a than in the upper packed layer part 15b, so that the void ratio is larger, that is, the gap is larger. Since the cross-sectional area is made large, it is possible to reduce clogging of the lower packed bed section 15a due to sludge generated when malodorous components are decomposed by microorganisms in the upper packed bed section 15b. Furthermore, since the carrier of the lower filled layer section 15a has a larger specific surface area with respect to ventilation resistance than the carrier of the upper filled layer section 15b,
The physicochemical reaction during the gas-liquid contact is efficiently carried out.

そして、下段の充填層部15aにおいて被処理ガス[θ
中の塩基性悪臭成分を中和除去した後、その洗浄水は脱
臭塔11の下部に設けられた洗浄水槽12に落下する。
Then, the gas to be treated [θ
After neutralizing and removing basic malodorous components therein, the washing water falls into a washing water tank 12 provided at the bottom of the deodorizing tower 11.

洗浄水槽12の洗浄水は上段の充填層部15bの洗浄及
びその微生物の活性を保持するため、繰返し使用される
が、この循環洗浄水のpH値及び塩濃度を微生物の活性
維持可能に保つため、撹拌槽12a内に中和剤を投入す
る。
The cleaning water in the cleaning water tank 12 is used repeatedly to clean the upper packed bed section 15b and to maintain the activity of the microorganisms, and the pH value and salt concentration of this circulating cleaning water are maintained to maintain the activity of the microorganisms. , a neutralizing agent is put into the stirring tank 12a.

なお、上段の充填層部15bは上記のように微生物によ
る分解に有利な構造にすることが望ましく、例えば上層
部の中性領域から下層部の酸性領域までそれぞれのpH
値に適合した微生物を固定保持させることにより、下段
の充填層部15aで除去しきれなかワた塩基性悪臭成分
、酸性悪臭成分及び下段の充填層部15aで除去できな
い中性悪臭成分を分解する。
It is preferable that the upper packed bed section 15b has a structure that is advantageous for decomposition by microorganisms as described above.
By fixing and retaining microorganisms that meet these values, basic malodorous components, acidic malodorous components that cannot be removed in the lower packed bed section 15a, and neutral malodorous components that cannot be removed in the lower packed bed section 15a are decomposed. .

[発明の効果] 以上のように本発明は脱臭塔内に配設された充填層を悪
臭成分の微生物分解を行う上段の充填層部と、この充填
層部にて生成する酸を含有する洗浄水により酸性悪臭成
分を吸収した酸性洗浄水を用いて塩基性悪臭成分を中和
除去する下段の充填層部とで形成し、これら2種類の充
填層部を有する1つの充填層を用いて脱臭を行うもので
あるから、従来の生物学的方法による処理コストの低置
という特徴をいかしたまま、上段の充填層部の負荷を軽
減することができるため、大量のガス、高濃度及び濃度
変動の大きなガスに対しても効率よく、酸性悪臭成分、
塩基性悪臭成分を脱臭処理することができると共に中性
悪臭成分を確実に脱臭処理でき、しかも特別の付属設備
を必要としないので、装置の小型化簡潔化が可能となる
という効果がある。
[Effects of the Invention] As described above, the present invention provides a deodorizing tower with an upper packed bed section that performs microbial decomposition of malodorous components, and a cleaning solution containing acid generated in this packed bed section. It is formed with a lower packed layer that neutralizes and removes basic malodorous components using acidic washing water that has absorbed acidic malodorous components with water, and deodorizes using one packed bed having these two types of packed bed sections. Because it performs this process, it is possible to reduce the load on the upper packed bed while taking advantage of the low processing costs of conventional biological methods. Efficiently removes acidic and malodorous components, even against large gases.
Since basic malodorous components can be deodorized and neutral malodorous components can be reliably deodorized, and no special accessory equipment is required, the device can be made smaller and simpler.

また、下段及び上段の充填層部の坦体の粒径を上段の充
填層部よりも下段の充填層部へいくに従い次第に大きく
し、空間率即ち、隙間の断面積が次第に大きくなるよう
にしているので、上段の充填層部において微生物によっ
て悪臭成分を分解質化させた時に発生する汚泥による下
段の充填層部の目詰りも減°少するという効果がある。
In addition, the grain size of the carrier in the lower and upper packed layer portions is made gradually larger toward the lower packed layer portion than the upper packed layer portion, so that the void ratio, that is, the cross-sectional area of the gap gradually increases. This has the effect of reducing clogging of the lower packed bed section due to sludge generated when malodorous components are decomposed by microorganisms in the upper packed bed section.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明の実施例を示す概略構成図、第2図は従
来のガスの脱臭装置を示す概略構成図である。 lO・・・被処理ガス、11・・・脱臭塔、12・・・
洗浄水槽、15・・・充填層、15a・・・下段の充填
層部、15b・・・上段の充填層部。
FIG. 1 is a schematic diagram showing an embodiment of the present invention, and FIG. 2 is a schematic diagram showing a conventional gas deodorizing apparatus. lO... Gas to be treated, 11... Deodorizing tower, 12...
Washing water tank, 15... Filled bed, 15a... Lower packed layer section, 15b... Upper filled layer section.

Claims (1)

【特許請求の範囲】 下部に被処理ガスの送入口と洗浄水槽が、また上部に処
理ガスの排出口が設けられ、該排出口と洗浄水槽との間
に多数の坦体からなる充填層が形成された脱臭塔を備え
、前記送入口から送入された被処理ガスを脱臭処理する
ガスの脱臭装置において、 前記充填層を下方に位置する物理化学的方法により悪臭
成分を除去する機能を有する下段の第1の充填層部と、
該充填層部より上方に位置し、洗浄水が散水され、生物
学的方法により悪臭成分を除去する機能を有する上段の
充填層部とで形成し、これら充填層部の坦体の粒径を上
段の充填層部よりも下段の充填層部のほうを大きくした
ことを特徴とするガスの脱臭装置。
[Claims] An inlet for the gas to be treated and a cleaning water tank are provided at the bottom, a discharge port for the processing gas is provided at the top, and a packed layer made of a large number of carriers is provided between the discharge port and the cleaning water tank. A gas deodorizing device that includes a formed deodorizing tower and deodorizes a gas to be treated fed through the inlet, the gas deodorizing device having a function of removing malodorous components by a physicochemical method located below the packed bed. a lower first packed bed section;
It is formed with an upper packed bed part located above the packed bed part, which is sprayed with washing water and has the function of removing malodorous components by a biological method, and the particle size of the carrier in these packed bed parts is A gas deodorizing device characterized in that a lower packed bed section is larger than an upper packed bed section.
JP63146998A 1988-06-16 1988-06-16 Deodorizing device for gas Pending JPH01315317A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63146998A JPH01315317A (en) 1988-06-16 1988-06-16 Deodorizing device for gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63146998A JPH01315317A (en) 1988-06-16 1988-06-16 Deodorizing device for gas

Publications (1)

Publication Number Publication Date
JPH01315317A true JPH01315317A (en) 1989-12-20

Family

ID=15420277

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63146998A Pending JPH01315317A (en) 1988-06-16 1988-06-16 Deodorizing device for gas

Country Status (1)

Country Link
JP (1) JPH01315317A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5304405A (en) * 1991-01-11 1994-04-19 Anelva Corporation Thin film deposition method and apparatus
US20090090240A1 (en) * 2007-10-04 2009-04-09 Hidayat Husain Biofiltration process and apparatus for odour or voc treatment
KR101139793B1 (en) * 2011-12-29 2012-05-03 코오롱아로마트릭스(주) Deodorizing apparatus with media multilayer type

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5304405A (en) * 1991-01-11 1994-04-19 Anelva Corporation Thin film deposition method and apparatus
US20090090240A1 (en) * 2007-10-04 2009-04-09 Hidayat Husain Biofiltration process and apparatus for odour or voc treatment
US8772015B2 (en) 2007-10-04 2014-07-08 Biorem Technologies Inc. Biofilter media to remove odour causing compounds from waste gas streams
KR101139793B1 (en) * 2011-12-29 2012-05-03 코오롱아로마트릭스(주) Deodorizing apparatus with media multilayer type

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