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JP3199992B2 - Biological deodorization method for hydrocarbon odorous substances - Google Patents
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JP3199992B2 - Biological deodorization method for hydrocarbon odorous substances - Google Patents

Biological deodorization method for hydrocarbon odorous substances

Info

Publication number
JP3199992B2
JP3199992B2 JP27074495A JP27074495A JP3199992B2 JP 3199992 B2 JP3199992 B2 JP 3199992B2 JP 27074495 A JP27074495 A JP 27074495A JP 27074495 A JP27074495 A JP 27074495A JP 3199992 B2 JP3199992 B2 JP 3199992B2
Authority
JP
Japan
Prior art keywords
circulating water
hydrogen peroxide
microorganisms
water
packed bed
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.)
Expired - Fee Related
Application number
JP27074495A
Other languages
Japanese (ja)
Other versions
JPH0985037A (en
Inventor
敏男 塚本
乃大 矢出
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.)
Ebara Corp
Original Assignee
Ebara Corp
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 Ebara Corp filed Critical Ebara Corp
Priority to JP27074495A priority Critical patent/JP3199992B2/en
Publication of JPH0985037A publication Critical patent/JPH0985037A/en
Application granted granted Critical
Publication of JP3199992B2 publication Critical patent/JP3199992B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

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、悪臭成分の生物学
的脱臭方法に係り、特に充填材を用いた炭化水素系臭気
成分を含む悪臭ガスの脱臭に際し、充填層に付着する微
生物を剥離する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for biological deodorization of a malodorous component, and in particular, removes microorganisms adhering to a packed bed when deodorizing a malodorous gas containing a hydrocarbon-based odorous component using a filler. About the method.

【0002】[0002]

【従来の技術】ベンゼンやトルエン等の炭化水素系臭気
物質を含むガスから、ベンゼンやトルエン等の炭化水素
系臭気物質を除去することを目的に長期間生物脱臭する
と、充填材に付着した微生物が増殖して充填層内の圧力
損失が著しく増加する。また、充填層内が部分的あるい
は全体的に閉塞するため、著しく脱臭機能が低下する。
従来、このような場合は充填材を系外に取り出し、水洗
などで機械的に付着微生物を剥離するか、次亜塩素酸ナ
トリウムで薬液洗浄する方法がとられた。しかし、前者
の付着微生物の剥離方法では、作業性に問題があり、後
者の方法では、次亜塩素酸の殺菌作用による付着微生物
への影響が大きく、運転再開時の脱臭性能が低下した
り、再度、微生物を流入臭気成分に適合させるための馴
致に時間がかかるという問題があった。
2. Description of the Related Art When a biological substance is deodorized for a long period of time to remove hydrocarbon-based odorous substances such as benzene and toluene from a gas containing hydrocarbon-based odorous substances such as benzene and toluene, microorganisms adhering to the filler are removed. Proliferation increases the pressure drop in the packed bed significantly. Further, since the inside of the packed layer is partially or entirely closed, the deodorizing function is significantly reduced.
Conventionally, in such a case, a method has been adopted in which the filler is taken out of the system, and the adhered microorganisms are mechanically peeled off by washing with water or a chemical solution is washed with sodium hypochlorite. However, in the former method of removing adhered microorganisms, there is a problem in workability, in the latter method, the effect on the adhered microorganisms by the hypochlorite bactericidal action is large, and the deodorizing performance at the time of restarting operation is reduced, Again, there is a problem that it takes a long time to adapt the microorganisms to the inflowing odor component.

【0003】[0003]

【発明が解決しようとする課題】本発明は、上記の問題
点を解決し、炭化水素系臭気物質を含む悪臭ガスに対し
て、充填層に付着する微生物を効率よく剥離除去して、
微生物の増殖による充填層の圧力損失増大の防止及び脱
臭性能を維持することのできる脱臭方法を提供すること
を課題とする。
SUMMARY OF THE INVENTION The present invention solves the above problems and efficiently removes and removes microorganisms adhering to a packed bed against a malodorous gas containing a hydrocarbon odorous substance.
An object of the present invention is to provide a deodorizing method capable of preventing an increase in pressure loss of a packed bed due to growth of microorganisms and maintaining deodorizing performance.

【0004】[0004]

【課題を解決するための手段】上記課題を解決するため
に、本発明では、生物膜を形成させた充填材に悪臭ガス
を通気する炭化水素系臭気の生物脱臭方法において、充
填材に付着する過剰の微生物を、過酸化水素を含む水と
接触させて剥離除去し、圧力損失の増大を防止すること
としたものである。前記方法において、過酸化水素を含
む水との接触は、充填層に過酸化水素の触媒としてアル
カリ剤又はカタラーゼを接触させてから行うのがよい。
In order to solve the above-mentioned problems, the present invention provides a method for deodorizing a hydrocarbon-based odor by passing a malodorous gas through a filler on which a biofilm is formed. Excessive microorganisms are brought into contact with water containing hydrogen peroxide to exfoliate and remove the microorganisms, thereby preventing an increase in pressure loss. In the above method, the contact with water containing hydrogen peroxide is preferably performed after bringing the packed bed into contact with an alkali agent or catalase as a catalyst for hydrogen peroxide.

【0005】なお、本発明において、炭化水素系臭気物
質とは、より具体的には、脂肪族炭化水素、低級脂肪酸
・エーテル系炭化水素、ケトン系炭化水素、アルコール
類等である。また、過酸化水素の機能は、生物膜の酸化
や膜間隙、膜基体間隙での発泡による生物膜の剥離、物
理的な振動による剥離、更には生じた泡への生物膜の吸
着浮上等が生じ余剰の生物膜を除去するものである。上
記のように、本発明では、微生物が付着した充填材を充
填した充填層において、充填層内の圧力損失の増大に際
して、充填材を充填したまま、酸化剤として、生物分解
が可能である過酸化水素水を使用し、過酸化水素の酸化
反応の触媒として、水酸化ナトリウム等のアルカリ剤又
はカタラーゼ酵素を使用することにより、付着微生物を
剥離することとしたものである。
[0005] In the present invention, hydrocarbon-based odorants are more specifically aliphatic hydrocarbons, lower fatty acid / ether-based hydrocarbons, ketone-based hydrocarbons, alcohols and the like. The functions of hydrogen peroxide include oxidation of the biofilm, separation of the biofilm due to foaming in the gap between the membranes and the gap between the membrane substrates, separation by physical vibration, and adsorption and floating of the biofilm to the generated bubbles. This is to remove the resulting excess biofilm. As described above, in the present invention, in a packed bed filled with a filler to which microorganisms are attached, when the pressure loss in the packed bed is increased, the biodegradation is possible as an oxidizing agent while the filler is filled. By using an aqueous hydrogen oxide solution and using an alkaline agent such as sodium hydroxide or a catalase enzyme as a catalyst for the oxidation reaction of hydrogen peroxide, the attached microorganisms are separated.

【0006】[0006]

【発明の実施の形態】本発明では、具体的には、生物脱
臭装置内を循環する水(以下、循環水)に、酸化剤であ
る過酸化水素水を注入して循環水が接触する充填層に過
酸化水素を供給し、その酸化力、及びその分解時に発生
する酸素ガスの発泡効果により充填材の付着微生物を分
解し、又は充填材から付着微生物を剥離除去するもので
ある。次に、前工程として触媒を併用する場合について
述べる。過酸化水素に対する触媒としてアルカリ剤とカ
タラーゼがある。アルカリ剤は、水酸化ナトリウム、水
酸化カリウム、水酸化カルシウムである。
DESCRIPTION OF THE PREFERRED EMBODIMENTS In the present invention, specifically, a hydrogen peroxide solution as an oxidizing agent is injected into water circulating in a biological deodorizing apparatus (hereinafter referred to as circulating water) to fill the circulating water. Hydrogen peroxide is supplied to the layer, and the microorganisms attached to the filler are decomposed by the oxidizing power and the foaming effect of oxygen gas generated at the time of decomposition thereof, or the attached microorganisms are peeled off from the filler. Next, a case where a catalyst is used in combination as a pre-process will be described. Catalysts for hydrogen peroxide include alkaline agents and catalase. Alkali agents are sodium hydroxide, potassium hydroxide and calcium hydroxide.

【0007】水酸化ナトリウムあるいはカタラーゼ酵素
を注入して、充填材付着物に水酸化ナトリウムあるいは
カタラーゼ酵素を十分浸透させる。浸透後、これら触媒
を含んだ循環水を排出し、次に酸化剤である過酸化水素
水を注入した循環水を循環させる。充填層において、過
酸化水素の酸化力とその分解時に発生する酸素ガスの発
泡効果により、充填材の付着微生物を分解し、充填材か
ら付着微生物を剥離除去するものである。触媒の浸漬工
程は、充填材付着物内での過酸化水素の分解による酸素
ガス発生を促進し、特に発泡による剥離の効果を高める
ことを意図したものである。
[0007] Sodium hydroxide or catalase enzyme is injected to allow the sodium hydroxide or catalase enzyme to sufficiently penetrate the deposits. After the permeation, the circulating water containing these catalysts is discharged, and then the circulating water into which the hydrogen peroxide solution as the oxidizing agent has been injected is circulated. In the packed bed, the microorganisms adhering to the filler are decomposed by the oxidizing power of hydrogen peroxide and the foaming effect of oxygen gas generated at the time of decomposition thereof, and the adhered microorganisms are peeled off from the filler. The catalyst immersion step is intended to promote the generation of oxygen gas due to the decomposition of hydrogen peroxide in the deposits on the filler, and particularly to enhance the effect of peeling by foaming.

【0008】次に、本発明の充填層からの微生物の剥離
について詳細に説明する。脱臭塔の循環水を循環しつ
つ、循環水に過酸化水素濃度が1重量%濃度以下(以
下、1%とする)となるように過酸化水素注入ポンプを
調節して過酸化水素水を注入し、過酸化水素を含む循環
水と充填材とを15分間程度接触させる。過酸化水素自
体の酸化力と分解による発泡により、充填材から剥離し
た微生物は微細粒子となり、循環水中に移行する。循環
水中でSS化した剥離微生物は循環水槽内の循環水と共
に系外に排出される。
Next, the exfoliation of microorganisms from the packed bed of the present invention will be described in detail. While circulating the circulating water of the deodorization tower, adjust the hydrogen peroxide injection pump so that the concentration of hydrogen peroxide is 1% by weight or less (hereinafter referred to as 1%) in the circulating water and inject the hydrogen peroxide water. Then, the circulating water containing hydrogen peroxide is brought into contact with the filler for about 15 minutes. Due to the oxidizing power of hydrogen peroxide itself and the foaming caused by decomposition, the microorganisms separated from the filler become fine particles and migrate into the circulating water. The exfoliated microorganisms formed into SS in the circulating water are discharged out of the system together with the circulating water in the circulating water tank.

【0009】触媒として、水酸化ナトリウムを使用する
場合は、生物脱臭装置の循環水を循環しつつ、循環水に
水酸化ナトリウムを注入する。循環水中の水酸化ナトリ
ウム濃度が3%以下となるようにポンプを調節して注入
し、循環水と充填材とを15分間程度接触させる。次
に、この循環水を排出する。その後、工業用水等の補給
水を循環水槽内に注入し、これに過酸化水素濃度が1%
となるように過酸化水素注入ポンプを調節して注入し、
循環水と充填材とを15分間程度接触させる。水酸化ナ
トリウムの代わりに、カタラーゼ酵素を触媒として使用
する場合も、同じ手順で行う。このとき、循環水中のカ
タラーゼ酵素濃度は、10%以下とする。
When sodium hydroxide is used as a catalyst, sodium hydroxide is injected into the circulating water while circulating in the circulating water of the biological deodorizer. The pump is adjusted so that the concentration of sodium hydroxide in the circulating water is 3% or less, and the circulating water is brought into contact with the filler for about 15 minutes. Next, the circulating water is discharged. After that, make-up water such as industrial water is injected into the circulating water tank, and the hydrogen peroxide concentration becomes 1%.
Adjust the hydrogen peroxide injection pump so that
The circulating water is brought into contact with the filler for about 15 minutes. The same procedure is used when a catalase enzyme is used as a catalyst instead of sodium hydroxide. At this time, the catalase enzyme concentration in the circulating water is 10% or less.

【0010】充填材の圧力損失の上昇原因は、流入ガス
中の炭化水素系臭気物質等が従属栄養細菌によって、資
化されることによりその菌が増殖するためである。この
従属栄養細菌は基質当たりの菌体増殖量が大きく、加え
て粘性の高い菌体外ポリマーを生成する。従来より、生
物スライムの除去に過酸化水素を主成分とする薬剤が使
用されるが、生物脱臭装置の圧力損失解消のために、過
酸化水素を用いて付着微生物を剥離させる方法は、未だ
提案されていない。剥離操作後再び脱臭処理を継続する
ために、生物分解が可能な過酸化水素の利用が有効であ
る。
[0010] The cause of the increase in the pressure loss of the filler is that the heterotrophic bacteria assimilate hydrocarbon-based odor substances and the like in the inflowing gas, and the bacteria grow. This heterotrophic bacterium has a large amount of cell growth per substrate and, in addition, produces a highly viscous extracellular polymer. Conventionally, a chemical containing hydrogen peroxide as a main component has been used for removing biological slime, but a method for removing adhered microorganisms using hydrogen peroxide to eliminate pressure loss of a biological deodorizing device is still proposed. It has not been. In order to continue the deodorizing treatment again after the stripping operation, it is effective to use biodegradable hydrogen peroxide.

【0011】次に、触媒として用いる水酸化ナトリウム
とカタラーゼ酵素の作用について説明する。一般にアル
カリは、微生物を溶解する効果がある。前工程として、
水酸化ナトリウム水溶液による洗浄を行うことで、付着
物を一部溶解剥離する。洗浄終了後、水酸化ナトリウム
水溶液を排出し、更に過酸化水素水で洗浄する。過酸化
水素水は、その酸化力によって付着物を分解剥離すると
同時に、前工程で付着微生物に浸透した水酸化ナトリウ
ムと付着微生物内で反応し、過酸化水素が分解して激し
く酸素ガスを排出する。この酸素ガス発生による発泡
が、付着物の剥離を促進する。
Next, the action of sodium hydroxide and a catalase enzyme used as a catalyst will be described. Generally, alkali has the effect of dissolving microorganisms. As a pre-process,
By washing with an aqueous solution of sodium hydroxide, the attached matter is partially dissolved and peeled off. After the washing is completed, the aqueous solution of sodium hydroxide is discharged, and further washed with a hydrogen peroxide solution. Hydrogen peroxide water decomposes and separates deposits due to its oxidizing power, and at the same time, reacts with sodium hydroxide that has penetrated the attached microorganisms in the attached microorganisms in the attached microorganisms, decomposing hydrogen peroxide and exhausting oxygen gas violently. . The foaming due to the generation of oxygen gas promotes the detachment of the deposit.

【0012】このように、水酸化ナトリウムによる前洗
浄工程は、水酸化ナトリウム自体の溶解剥離効果と同時
に、触媒として、付着物に接触した過酸化水素の分解を
促進し、洗浄効果を高める作用がある。カタラーゼ酵素
による前洗浄工程では、カタラーゼ酵素自体に微生物を
分解する性質がないために、付着物剥離は期待できない
が、水酸化ナトリウムと同様に過酸化水素の分解を促進
し、酸素ガスを発生させる。したがって、水酸化ナトリ
ウムを使用した場合と同様の効果がある。また、カタラ
ーゼ酵素は、元来、好気性微生物が有している物質であ
り、水酸化ナトリウムに比べて微生物への影響が極めて
少ないことが有利な点である。
As described above, the pre-cleaning step using sodium hydroxide has the effect of promoting the decomposition of hydrogen peroxide that has come into contact with the deposits as a catalyst and at the same time enhancing the cleaning effect, as well as the effect of dissolving and removing sodium hydroxide itself. is there. In the pre-cleaning step with the catalase enzyme, the catalase enzyme itself does not have the property of decomposing microorganisms, so it is not expected that the adherents are peeled off.However, like the sodium hydroxide, it promotes the decomposition of hydrogen peroxide and generates oxygen gas. . Therefore, the same effect as when sodium hydroxide is used is obtained. Catalase enzyme is a substance originally possessed by aerobic microorganisms, and is advantageous in that the effect on microorganisms is extremely small as compared with sodium hydroxide.

【0013】次に、本発明を図面を参照して詳細に説明
する。図1に、本方法に用いる装置の概略断面図を示
す。図1において、脱臭塔3には、充填材の充填された
充填層2とその上部に充填層に循環水を散水するための
散水部4が設けられ、また、下部に、循環水層8が設け
られる。そして、循環水槽8から散水部4にポンプ6を
介して循環水が循環されている。原ガス流入管1のダン
パーを閉にしたのち、循環ポンプ6を30リットル/m
inで運転しつつ、過酸化水素水注入ポンプ12を用い
て、循環水中の過酸化水素濃度が1%になるように注入
する。循環水中の過酸化水素濃度が1%程度になると、
付着微生物の分解剥離が生じ、そのために循環水のSS
が増加する。
Next, the present invention will be described in detail with reference to the drawings. FIG. 1 shows a schematic sectional view of an apparatus used in the present method. In FIG. 1, a deodorization tower 3 is provided with a packed bed 2 filled with a filler and a sprinkling section 4 for spraying circulating water to the packed bed above the packed bed 2, and a circulating water layer 8 below the packed bed. Provided. The circulating water is circulated from the circulating water tank 8 to the sprinkling section 4 via the pump 6. After closing the damper of the raw gas inflow pipe 1, the circulation pump 6 is turned on at 30 l / m.
While operating at “in”, the hydrogen peroxide water injection pump 12 is used to inject hydrogen peroxide in the circulating water so that the concentration becomes 1%. When the concentration of hydrogen peroxide in the circulating water reaches about 1%,
Decomposition and detachment of attached microorganisms occur, which causes SS in circulating water
Increase.

【0014】循環水のSSが50mg/リットルになっ
たら、排水弁7を開にして、循環水を排出する。排出
後、補給水1リットルを注入し、塔内を循環させて残留
過酸化水素水を洗い流す。補給水の注入、循環、排出を
繰り返した後、定常の脱臭運転に戻る。次に、触媒使用
の場合について述べる。循環ポンプ6を30リットル/
minで運転しつつ、水酸化ナトリウム(カタラーゼ酵
素)注入ポンプ13を用いて、循環水中の水酸化ナトリ
ウムが3%(カタラーゼ酵素にあっては、10%)にな
るように注入する。15分程度循環を続けた後、排水弁
7を開にして、水酸化ナトリウム水溶液(あるいは、カ
タラーゼ酵素水溶液)を排出する。
When the SS of the circulating water reaches 50 mg / liter, the drain valve 7 is opened to discharge the circulating water. After the discharge, 1 liter of make-up water is injected and circulated in the tower to wash away residual hydrogen peroxide water. After repeating injection, circulation and discharge of make-up water, the operation returns to the regular deodorizing operation. Next, the case of using a catalyst will be described. 30 liters of circulation pump 6
The sodium hydroxide (catalase enzyme) injection pump 13 is used to inject sodium hydroxide in the circulating water to 3% (10% for catalase enzyme) while operating at min. After continuing the circulation for about 15 minutes, the drain valve 7 is opened to discharge the aqueous sodium hydroxide solution (or the aqueous catalase enzyme solution).

【0015】再び排水弁7を閉にして、循環ポンプ6を
30リットル/minで運転しつつ、過酸化水素水注入
ポンプ12を用いて、循環水中の過酸化水素濃度が1%
になるように注入する。循環水中の過酸化水素濃度が1
%程度になると、付着微生物の分解剥離が生じ、そのた
めに循環水のSSが増加する。循環水のSSが50mg
/リットルになったら、排水弁7を開にして、循環水を
排出する。排出後、補給水10を注入し、塔内を循環さ
せて残留過酸化水素水を洗い流す。補給水の注入、循
環、排出を繰り返した後、定常の脱臭運転に戻る。
With the drain valve 7 closed again, while operating the circulation pump 6 at 30 liter / min, the hydrogen peroxide concentration in the circulating water is reduced to 1% by using the hydrogen peroxide water injection pump 12.
Inject so that it becomes. Hydrogen peroxide concentration in circulating water is 1
%, The adhered microorganisms are decomposed and separated, and the SS of the circulating water increases. 50mg of circulating water SS
/ Liter, the drain valve 7 is opened to discharge the circulating water. After the discharge, make-up water 10 is injected and circulated in the tower to wash away residual hydrogen peroxide water. After repeating injection, circulation and discharge of make-up water, the operation returns to the regular deodorizing operation.

【0016】[0016]

【実施例】以下、本発明を実施例により具体的に説明す
る。 実施例1 図1の実験装置を用いて生物学的に脱臭実験を約1ケ月
間行った。揮発性有機化合物であるベンゼン、トルエン
の試薬を空気に注入して、ベンゼン、トルエン濃度が2
0〜50ppmとなるように調整したものを原ガスとし
た。脱臭実験の条件は次の通りである。 LV : 0.2m/sec、 循環水散水速度 : 30リットル/min、 原ガス温度 : 30℃ 充填材 : テラレット(登録商標、日鉄化工機株式会社製) 充填層高 : 1m
The present invention will be described below in more detail with reference to examples. Example 1 A biological deodorization experiment was conducted for about one month using the experimental apparatus of FIG. Inject the reagents of benzene and toluene, which are volatile organic compounds, into the air and adjust the concentration of benzene and toluene to 2
What was adjusted to be 0 to 50 ppm was used as a raw gas. The conditions of the deodorization experiment are as follows. LV: 0.2 m / sec, circulating water sprinkling speed: 30 liter / min, raw gas temperature: 30 ° C. Filling material: Terralet (registered trademark, manufactured by Nippon Steel Chemical Machine Co., Ltd.) Filling layer height: 1 m

【0017】この条件で生物学的な脱臭を行い、充填層
高さ1mあたりの圧力損失を50mmH2 Oに上昇させ
た状態で、充填層の付着微生物剥離の実験を行った。同
一脱臭実験で実験装置を運転し、循環水に過酸化水素水
をその濃度が1%となるように注入した。この時の循環
水のSSは3mg/リットルであった。注入直後、付着
物から発泡が生じ、付着物の分解、剥離が生じはじめ、
循環水のSSが30mg/リットルまで増加した。注入
開始から30分後、循環水のSS濃度が60mg/リッ
トル程度になったので循環水槽より循環水を排出し、新
たに補給水を注入した。この後、循環水の排出、注入に
よる残留過酸化水素の洗浄を一度行った後、再び定常の
脱臭実験に戻った。この時の循環水中のSSは3mg/
リットル、充填層高さ1mあたりの圧力損失は10mm
2 Oとなった。
Under these conditions, biological deodorization was carried out, and an experiment of detachment of microorganisms adhering to the packed bed was carried out in a state where the pressure loss per 1 m height of the packed bed was raised to 50 mmH 2 O. The experimental apparatus was operated in the same deodorization experiment, and hydrogen peroxide was injected into the circulating water so that the concentration became 1%. The circulating water SS at this time was 3 mg / liter. Immediately after the injection, foaming occurs from the attached matter, decomposition and detachment of the attached matter begin to occur,
The circulating water SS increased to 30 mg / liter. Thirty minutes after the start of the injection, the circulating water was discharged from the circulating water tank because the SS concentration of the circulating water became approximately 60 mg / liter, and fresh makeup water was injected. After that, the residual hydrogen peroxide was washed once by discharging and injecting the circulating water, and then returned to the regular deodorization experiment. The SS in the circulating water at this time was 3 mg /
Pressure loss per liter, packed bed height 1m is 10mm
H 2 O was obtained.

【0018】実施例2 触媒を併用した場合について述べる。同一脱臭実験で実
験装置を運転し、水酸化ナトリウム水溶液で前工程洗浄
を行った。15分間の洗浄で循環水中のSSは15mg
/リットルであった。水酸化ナトリウム水溶液を排出
後、循環水に過酸化水素水を1%となるように注入し
た。この時の循環水のSSは3mg/リットルであっ
た。注入直後、付着物から発泡が生じ、付着物の分解、
剥離が生じはじめ、循環水のSSが50mg/リットル
まで増加した。注入開始から15分後、循環水のSS濃
度が100mg/リットル程度になったので循環水槽よ
り循環水を排出し、新たに補給水を注入した。この後、
循環水の排出、注入による残留過酸化水素の洗浄を一度
行った後、再び定常の脱臭実験に戻った。この時の循環
水中のSSは3mg/リットル、充填層1mあたりの圧
力損失は5mmH2 Oとなった。
Example 2 A case where a catalyst is used in combination will be described. The experimental apparatus was operated in the same deodorization experiment, and pre-process washing was performed with an aqueous sodium hydroxide solution. After washing for 15 minutes, SS in circulating water is 15mg
/ Liter. After discharging the aqueous solution of sodium hydroxide, an aqueous solution of hydrogen peroxide was injected into the circulating water to a concentration of 1%. The circulating water SS at this time was 3 mg / liter. Immediately after injection, foam is generated from the deposit,
Separation began to occur and the circulating water SS increased to 50 mg / liter. 15 minutes after the start of the injection, the circulating water was discharged from the circulating water tank because the SS concentration of the circulating water became approximately 100 mg / liter, and fresh makeup water was injected. After this,
After the residual hydrogen peroxide was washed once by discharging and injecting circulating water, the operation was returned to the regular deodorization experiment. The SS in the circulating water at this time was 3 mg / liter, and the pressure loss per 1 m of the packed bed was 5 mmH 2 O.

【0019】実施例3 実施例2の前工程洗浄として水酸化ナトリウムの代わり
にカタラーゼ酵素を用いた場合について以下に示す。実
施例2と同じ条件で脱臭実験に生物脱臭を行い、充填層
高さ1mあたりの圧力損失を50mmH2 Oに上昇させ
た状態で、充填層の付着微生物剥離の実験を行った。同
一脱臭実験で実験装置を運転し、循環水にカタラーゼ酵
素を10%となるように注入した。この時の循環水のS
Sは3mg/リットルであった。注入後15分間循環し
たが循環水中のSS濃度の変化は無かった。カタラーゼ
酵素水溶液を排出後、循環水に過酸化水素水を1%とな
るように注入した。注入直後、付着物から発泡が生じ、
付着物の分解、剥離が生じはじめ、循環水のSSが30
mg/リットルまで増加した。注入開始から15分後、
循環水のSS濃度が80mg/リットル程度になったの
で循環水槽より循環水を排出し、新たに補給水を注入し
た。この後、循環水の排出、注入による残留過酸化水素
の洗浄を一度行った後、再び定常の脱臭実験に戻った。
この時の循環水中のSSは3mg/リットル、充填層1
mあたりの圧力損失は、8mmH2 Oとなった。
Example 3 A case where a catalase enzyme was used instead of sodium hydroxide as the pre-step washing in Example 2 is described below. Perform biological deodorization deodorization experiment under the same conditions as in Example 2, in a state of increasing the pressure loss per packed bed height 1m to 50 mm H 2 O, an experiment was performed adhering microorganisms peeling of the filling layer. The experimental apparatus was operated in the same deodorization experiment, and the catalase enzyme was injected into the circulating water so as to be 10%. The circulating water S at this time
S was 3 mg / liter. Circulation was performed for 15 minutes after injection, but there was no change in SS concentration in the circulating water. After discharging the catalase enzyme aqueous solution, 1% of hydrogen peroxide solution was injected into the circulating water. Immediately after injection, foam is generated from the deposit,
Decomposition and delamination of deposits begin to occur, and the circulating water
mg / liter. 15 minutes after the start of infusion,
When the SS concentration of the circulating water became about 80 mg / liter, the circulating water was discharged from the circulating water tank, and fresh makeup water was injected. After that, the residual hydrogen peroxide was washed once by discharging and injecting the circulating water, and then returned to the regular deodorization experiment.
The SS in the circulating water at this time was 3 mg / liter, and the packed bed 1
The pressure loss per m was 8 mmH 2 O.

【0020】比較例1 実施例1と同じ条件で一か月にわたり脱臭処理したとこ
ろ、充填層1mあたりの圧力損失が50mmH2 Oとな
ったので、微生物の剥離を行った。原ガス流入管のダン
パーを閉にした後、循環水中に次亜塩素酸ナトリウム
を、有効塩素濃度が3%となるように注入した。循環ポ
ンプを運転して次亜塩素酸ナトリウムを含んだ循環水を
30リットル/minで60分間、充填層に散水した。
循環水槽内の循環水を排出した後、補給水を注入し残留
次亜塩素酸ナトリウムを水洗浄した。その結果、同一実
験条件下で充填層1mあたりの圧力損失が10mmH2
Oまで回復した。
Comparative Example 1 When deodorizing treatment was carried out for one month under the same conditions as in Example 1, the pressure loss per 1 m of the packed bed became 50 mmH 2 O, so that the microorganisms were removed. After closing the damper of the raw gas inflow pipe, sodium hypochlorite was injected into the circulating water so that the effective chlorine concentration became 3%. By operating the circulation pump, circulating water containing sodium hypochlorite was sprinkled on the packed bed at 30 L / min for 60 minutes.
After discharging the circulating water in the circulating water tank, make-up water was injected to wash residual sodium hypochlorite with water. As a result, under the same experimental conditions, the pressure loss per 1 m of the packed bed was 10 mmH 2
It recovered to O.

【0021】表1に実施例1〜3(本発明)と比較例1
(従来法)について、圧力損失と洗浄に要した時間、及
び洗浄後のベンゼン除去性能の比較を示す。本発明の方
法では、従来法の約2分の1の洗浄時間で同程度の圧力
損失解消が実現でき、除去後のベンゼン除去性能にも優
れ、洗浄直後の除去率で3倍以上、再馴致に要する時間
が5分の1以下であった。
Table 1 shows Examples 1 to 3 (invention) and Comparative Example 1.
A comparison of the pressure loss, the time required for cleaning, and the benzene removal performance after cleaning is shown for (conventional method). According to the method of the present invention, the same pressure loss can be eliminated in about half the cleaning time of the conventional method, the benzene removal performance after the removal is excellent, and the removal rate immediately after the cleaning is more than three times that of the conventional method. Was less than 1/5.

【0022】[0022]

【表1】 1) ( )内水洗時間 2) 除去率が90%に達するまでの時間[Table 1] 1) () Inner water washing time 2) Time until removal rate reaches 90%

【0023】[0023]

【発明の効果】本発明による効果は次の通り。 (1)非常に簡単な方法で、容易に短時間で付着微生物
の剥離除去が可能である。 (2)剥離後の脱臭性能低下の程度が小さい。 (3)付着微生物剥離後の脱臭性能の回復(再馴致)に
要する時間が比較的短い。
The effects of the present invention are as follows. (1) Adhering microorganisms can be easily removed in a short time by a very simple method. (2) The degree of deterioration in deodorizing performance after peeling is small. (3) The time required for restoring the deodorizing performance after detachment of the adhered microorganisms (reestablishment) is relatively short.

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

【図1】本発明の方法に用いる装置の概略断面図。FIG. 1 is a schematic sectional view of an apparatus used in the method of the present invention.

【符号の説明】[Explanation of symbols]

1:原ガス、2:充填層、3:脱臭塔、4:散水部、
5:ガス出口部、6:循環水ポンプ、7:排水分、8:
循環水槽、9:NaOH(カタラーゼ酵素)注入ライ
ン、10:H2 2 注入ライン、11:補給水、12:
2 2 注入ポンプ、13:NaOH(カタラーゼ酵
素)注入ポンプ、14:NaOH(カタラーゼ酵素)貯
槽、15:H2 2 貯槽
1: raw gas, 2: packed bed, 3: deodorization tower, 4: sprinkling unit,
5: Gas outlet, 6: Circulating water pump, 7: Drainage, 8:
Circulating water tank, 9: NaOH (catalase enzyme) injection line, 10: H 2 O 2 injection line, 11: makeup water, 12:
H 2 O 2 injection pump, 13: NaOH (catalase enzyme) injection pump, 14: NaOH (catalase enzyme) storage tank, 15: H 2 O 2 storage tank

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B01D 53/38 B01D 53/34 ZAB C12N 1/00 ──────────────────────────────────────────────────続 き Continued on the front page (58) Fields surveyed (Int. Cl. 7 , DB name) B01D 53/38 B01D 53/34 ZAB C12N 1/00

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 生物膜を形成させた充填材に悪臭ガスを
通気する炭化水素系臭気の生物脱臭方法において、充填
材に付着する過剰の微生物を、過酸化水素を含む水と接
触させて剥離除去し、圧力損失の増大を防止することを
特徴とする生物脱臭方法。
1. A method for deodorizing a hydrocarbon-based odor by passing a malodorous gas through a filler on which a biofilm is formed, wherein excessive microorganisms adhering to the filler are peeled off by contact with water containing hydrogen peroxide. A biological deodorizing method characterized by removing and preventing an increase in pressure loss.
【請求項2】 前記過酸化水素を含む水との接触は、充
填層に過酸化水素の触媒としてアルカリ剤又はカタラー
ゼを接触させてから行うことを特徴とする請求項1記載
の生物脱臭方法。
2. The biological deodorization method according to claim 1, wherein the contact with the water containing hydrogen peroxide is performed after bringing the packed bed into contact with an alkali agent or catalase as a catalyst for hydrogen peroxide.
JP27074495A 1995-09-26 1995-09-26 Biological deodorization method for hydrocarbon odorous substances Expired - Fee Related JP3199992B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27074495A JP3199992B2 (en) 1995-09-26 1995-09-26 Biological deodorization method for hydrocarbon odorous substances

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP27074495A JP3199992B2 (en) 1995-09-26 1995-09-26 Biological deodorization method for hydrocarbon odorous substances

Publications (2)

Publication Number Publication Date
JPH0985037A JPH0985037A (en) 1997-03-31
JP3199992B2 true JP3199992B2 (en) 2001-08-20

Family

ID=17490378

Family Applications (1)

Application Number Title Priority Date Filing Date
JP27074495A Expired - Fee Related JP3199992B2 (en) 1995-09-26 1995-09-26 Biological deodorization method for hydrocarbon odorous substances

Country Status (1)

Country Link
JP (1) JP3199992B2 (en)

Also Published As

Publication number Publication date
JPH0985037A (en) 1997-03-31

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