JPH08281066A - Treatment of waste gases containing volatile organic chlorine compound and treating device therefor - Google Patents

Treatment of waste gases containing volatile organic chlorine compound and treating device therefor

Info

Publication number
JPH08281066A
JPH08281066A JP7115245A JP11524595A JPH08281066A JP H08281066 A JPH08281066 A JP H08281066A JP 7115245 A JP7115245 A JP 7115245A JP 11524595 A JP11524595 A JP 11524595A JP H08281066 A JPH08281066 A JP H08281066A
Authority
JP
Japan
Prior art keywords
packed
exhaust gas
treating device
gas
treatment
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn
Application number
JP7115245A
Other languages
Japanese (ja)
Inventor
Shigeki Yamashita
茂樹 山下
Masami Kitagawa
政美 北川
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.)
Ebara Corp
Ebara Research Co Ltd
Original Assignee
Ebara Corp
Ebara Research Co 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 Ebara Corp, Ebara Research Co Ltd filed Critical Ebara Corp
Priority to JP7115245A priority Critical patent/JPH08281066A/en
Publication of JPH08281066A publication Critical patent/JPH08281066A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Abstract

PURPOSE: To efficiently treat volatile org. chlorine compds. with low energy by irradiating waste gases contg. the volatile org. chlorine compds. with UV rays to change the properties of the volatile org. chlorine compds., then passing the waste gases through a biological treating device packed with packing materials deposited with microorganisms in a wet state. CONSTITUTION: The air contg. trichloroethylene, etc., is passed through the inside of a UV irradiation device 3 having passages and is irradiated with the UV rays by a low-pressure mercury lamp 2. The gas cracked to the org. chlorine compds., such as dichloroacetic acid with higher hydrophilic nature is introduced into the lower part of the biological treating device 4. The device 4 is internally provided with a packed phase 5 packed with the packing materials in which the microorganisms are deposited. This packed phase 5 is maintained in a wet state by sprinkling makeup water 8 replenished to a water receiving tank in the bottom of the biological treating device 4 as circulating water 7 from the sprinkling section in the upper part of the packed phase 5. The org. chlorine compds. with higher hydrophilic nature introduced into the lower part of the biological treating device 4 is passed through the packed phase 5, by which the gas is biologically treated. The gas is then discharged outside the system.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、土壌汚染処理排ガス、
ドライクリニング排ガス及び金属洗浄工場排ガスなどの
揮発性有機塩素化合物(例えば、ドライクリニングで使
用される1,1,1トリクロロエタン、テトラクロロエ
チレンや金属洗浄工場で使用されるトリクロロエチレ
ン、メチレンクロライド、その他一般溶媒として使用さ
れる1,2ジクロロエタン、1,1,2,2テトラクロ
ロエタン、医薬としても使用されるクロロホルム等)を
含有する排ガスの処理に適用される。
BACKGROUND OF THE INVENTION The present invention relates to exhaust gas for soil pollution treatment,
Volatile organochlorine compounds such as dry cleaning exhaust gas and metal cleaning plant exhaust gas (for example, 1,1,1 trichloroethane used in dry cleaning, tetrachloroethylene and trichlorethylene used in metal cleaning plant, methylene chloride, and other general solvents 1,2 dichloroethane, 1,1,2,2 tetrachloroethane, chloroform also used as a medicine, etc.).

【0002】[0002]

【従来の技術】従来、揮発性有機塩素化合物を含有する
排ガスの処理には、燃焼法、活性炭吸着法あるいはそれ
らを組み合わせた方法などが用いられている。しかしこ
れらの方法は、低濃度、大風量の排ガスに対しては必ず
しも適した方法とはいえない。生物処理は比較的低濃
度、大風量の排ガスを低エネルギーで処理できる方法で
あり、主に硫化水素、メチルメルカプタン、アンモニア
などを含有する悪臭ガスの処理に実用化されている。し
かし、揮発性有機塩素化合物の生物処理は研究段階にあ
り、実用化には至っていない。また、紫外線は低濃度の
物質を効率的に酸化分解させることのできる方法であ
り、今後排ガス処理の分野でも応用が期待される方法で
ある。本発明者らは、揮発性有機塩素化合物を含有する
気相中に水素源を供給した後、該気相を紫外線に曝露し
て前記気相中の揮発性有機塩素化合物を分解することを
特徴とする揮発性有機塩素化合物の処理方法を特願平5
−329605号で提案した。
2. Description of the Related Art Conventionally, a combustion method, an activated carbon adsorption method or a combination thereof is used for treating exhaust gas containing a volatile organic chlorine compound. However, these methods are not necessarily suitable for exhaust gas with low concentration and large air flow. Biological treatment is a method capable of treating exhaust gas having a relatively low concentration and a large air volume with low energy, and has been put to practical use mainly for treating malodorous gases containing hydrogen sulfide, methyl mercaptan, ammonia and the like. However, biological treatment of volatile organochlorine compounds is still in the research stage and has not been put to practical use. Further, ultraviolet rays are a method capable of efficiently oxidizing and decomposing low-concentration substances, and are expected to be applied in the field of exhaust gas treatment in the future. The inventors of the present invention are characterized by supplying a hydrogen source into a gas phase containing a volatile organochlorine compound and then exposing the gas phase to ultraviolet rays to decompose the volatile organochlorine compound in the gas phase. Patent application 5
-329605.

【0003】[0003]

【発明が解決しようとする課題】従来の生物処理方法は
概ね以下のような技術である。すなわち、生物処理方法
は微生物の担体を充填した充填層に排ガスを通気し、担
体に付着した生物により排ガス中の処理対象成分を酸化
分解させ、その際充填塔に散水し、散水を通じて老廃物
の除去及び栄養塩の補給を行う方法である。しかし、例
えば前記1,1,1トリクロロエタン、テトラクロロエ
チレン及びトリクロロエチレンなどの揮発性有機塩素化
合物を分解させる際には、微生物の有機塩素化合物分解
能を誘導する物質(以下「誘導物質」と記す)を供給し
なければならない。誘導物質としては、メタンガスある
いはフェノールなどが用いられている。
The conventional biological treatment methods are generally the following techniques. That is, the biological treatment method is to ventilate the exhaust gas into a packed bed filled with a carrier of microorganisms, to oxidize and decompose the components to be treated in the exhaust gas by the organisms attached to the carrier, at that time sprinkling water in the packed tower, waste products through watering. It is a method of removing and supplementing nutrients. However, for example, when decomposing volatile organic chlorine compounds such as 1,1,1 trichloroethane, tetrachloroethylene and trichloroethylene, a substance (hereinafter referred to as "inducing substance") that induces decomposition of the organic chlorine compounds of the microorganism is supplied. There must be. Methane gas, phenol, or the like is used as the inducer.

【0004】この誘導物質の必要性は生物処理の実用化
を妨げる原因の一つとなっている。その理由は以下の通
りである。(i) 誘導物質を供給するためにコストが必要
である。(ii)メタンガスは爆発の危険性があり、取扱に
注意が必要である。(iii) フェノールは環境に対して有
害な物質であるため、環境中に放出して二次汚染を発生
させないように注意が必要である。また、紫外線分解
は、揮発性有機塩素化合物を完全分解する(炭酸ガス、
水及び塩化水素などに分解する。)ためには長い照射時
間(4〜8分間)が必要であった。従って、完全分解さ
せることは必ずしも実用的とはいえない。本発明は、前
記の問題点を解決し、揮発性有機塩素化合物を効果的に
処理する排ガスの処理方法及び排ガスの処理装置を提供
することを課題とする。
The need for this inducer is one of the causes of impeding the practical application of biological treatment. The reason is as follows. (i) Cost is required to supply the inducer. (ii) Methane gas has a risk of explosion and should be handled with care. (iii) Phenol is a harmful substance to the environment, so care must be taken not to release it into the environment to cause secondary pollution. UV decomposition completely decomposes volatile organic chlorine compounds (carbon dioxide,
Decomposes in water and hydrogen chloride. ) Required a long irradiation time (4 to 8 minutes). Therefore, complete decomposition is not always practical. It is an object of the present invention to solve the above problems and provide an exhaust gas treatment method and an exhaust gas treatment apparatus that effectively treat a volatile organic chlorine compound.

【0005】[0005]

【課題を解決するための手段】本発明者らは、「揮発性
有機塩素化合物は短時間の紫外線照射では完全に分解し
ないが、性質の異なる物質に変化する。」ことを見出し
た。そこで発明者らは、短時間の紫外線照射によって物
性の変化した揮発性有機塩素化合物を生物処理法によっ
て処理させてみたところ、誘導物質を必要とせず、しか
も高効率で処理可能であることが明らかとなり本発明に
到った。すなわち、(1)揮発性有機塩素化合物を含む
排ガスに対して紫外線を照射し、該揮発性有機塩素化合
物の物性を変化させる工程と、続いて微生物を湿潤状態
で保持した充填材を充填した生物処理装置を通過させて
処理する工程を有することを特徴とする揮発性有機塩素
化合物を含む排ガスの処理方法及び、(2)揮発性有機
塩素化合物を含む排ガスに対して紫外線を照射する照射
装置と、充填塔内に微生物を保持できる充填材を充填し
た充填相を設け、該充填相の上部に散水部を配備すると
共に、充填塔下部に受水槽を配備し、該充填材を湿潤状
態に維持した生物処理装置とを有し、順次前記紫外線照
射装置と、前記生物処理装置とに前記排ガスを通過させ
て処理するよう配置することを特徴とする揮発性有機塩
素化合物を含む排ガスの処理装置である。
The present inventors have found that "a volatile organochlorine compound is not completely decomposed by irradiation of ultraviolet rays for a short time, but is transformed into a substance having a different property." Therefore, the inventors of the present invention tried to treat a volatile organochlorine compound whose physical properties were changed by irradiation with ultraviolet rays for a short time by a biological treatment method, and found that it does not require an inducer and can be treated with high efficiency. That is the present invention. That is, (1) a step of irradiating an exhaust gas containing a volatile organochlorine compound with ultraviolet rays to change the physical properties of the volatile organochlorine compound, and subsequently, an organism filled with a filler in which microorganisms are kept in a wet state. A method for treating exhaust gas containing a volatile organic chlorine compound, which comprises a step of passing through a treatment device for treatment, and (2) an irradiation device for irradiating the exhaust gas containing a volatile organic chlorine compound with ultraviolet rays. , A packed phase filled with a packing material capable of holding microorganisms is provided in the packed tower, a sprinkler section is provided above the packed phase, and a water receiving tank is provided under the packed tower to maintain the packed material in a wet state. A treatment apparatus for exhaust gas containing a volatile organochlorine compound, which is characterized in that the exhaust gas is passed through the ultraviolet treatment apparatus and the biological treatment apparatus in order to process the exhaust gas. It is a device.

【0006】本発明の揮発性有機塩素化合物を含む排ガ
スの処理に使用する紫外線照射用のUVランプとして
は、波長260nmから1nmまでの紫外線を含む光線
を放射できるランプであれば特に制限されないが、市販
のUVランプとしては、例えば紫外線酸化用ランプQG
L25W−3(岩崎電気株式会社製)、低圧水銀ランプ
GL20ZH(山共電気株式会社製)などを好ましいも
のとして挙げることができる。これらのランプは以下の
ように、例えば185nmの波長の紫外線を放射でき
る。照射条件としては例えば、100ppmのトリクロ
ロエチレンを含むガス1リットルあたり波長185nm
の紫外線を10ジュール(J)照射することで十分効果
が期待できる。また、トリクロロエチレン濃度が約40
ppm以下では、濃度が低下すると効果は低下する。し
かし約40ppm以上では、濃度が上昇しても効果は低
下しなかった。これはトリクロロエチレンの反応形態が
ラジカル連鎖反応であることによると推察されている。
The UV lamp for UV irradiation used for treating the exhaust gas containing the volatile organochlorine compound of the present invention is not particularly limited as long as it is a lamp capable of emitting a light beam containing UV rays having a wavelength of 260 nm to 1 nm. Examples of commercially available UV lamps include UV oxidation lamp QG
L25W-3 (manufactured by Iwasaki Electric Co., Ltd.), low-pressure mercury lamp GL20ZH (manufactured by Yamakyo Electric Co., Ltd.) and the like can be mentioned as preferable ones. These lamps can emit UV light, for example with a wavelength of 185 nm, as follows. The irradiation conditions include, for example, a wavelength of 185 nm per liter of a gas containing 100 ppm of trichlorethylene.
It is possible to expect a sufficient effect by irradiating the ultraviolet rays of 10 Joules (J). Also, the concentration of trichlorethylene is about 40.
Below ppm, the effect decreases as the concentration decreases. However, at about 40 ppm or more, the effect did not decrease even if the concentration increased. It is speculated that this is because the reaction form of trichlorethylene is a radical chain reaction.

【0007】[0007]

【作用】揮発性有機塩素化合物に紫外線を照射すると、
周囲に存在する酸素あるいは水などと反応し、酸化物あ
るいは水酸化物などが生成する。例えば、1,1,1ト
リクロロエタンに紫外線を照射するとトリクロロ酢酸な
どが、またトリクロロエチレンの場合にはジクロロ酢酸
が生成した。これらの物質は、1,1,1トリクロロエ
タンやトリクロロエチレンとそれぞれ比較して親水性が
高く、またトリクロロ酢酸やジクロロ酢酸は1,1,1
トリクロロエタンやトリクロロエチレンよりも生物によ
る分解は容易である。従って揮発性有機塩素化合物は紫
外線照射後、そのガスを生物処理装置に供給することに
より、紫外線処理生成物は容易に生物分解される。
[Function] When a volatile organic chlorine compound is irradiated with ultraviolet rays,
Reacts with oxygen or water existing in the surroundings to generate oxides or hydroxides. For example, when 1,1,1 trichloroethane was irradiated with ultraviolet rays, trichloroacetic acid and the like were produced, and in the case of trichloroethylene, dichloroacetic acid was produced. These substances are more hydrophilic than 1,1,1 trichloroethane and trichloroethylene, respectively, and trichloroacetic acid and dichloroacetic acid are 1,1,1
Biodegradation is easier than trichloroethane or trichlorethylene. Therefore, by irradiating the volatile organic chlorine compound with ultraviolet rays and supplying the gas to the biological treatment apparatus, the ultraviolet-treated product is easily biodegraded.

【0008】[0008]

【実施例】以下に実施例を挙げて本発明を説明するが、
本発明はこれによって限定されるものではない。
The present invention will be described below with reference to examples.
The present invention is not limited to this.

【0009】実施例1 100ppmのトリクロロエチレン及び30ppmの
1,1,1−トリクロロエタンを含む空気を、図1に示
す紫外線照射と生物処理を組合せて処理する装置を用
い、第1表の実施例1に示す処理条件で処理した。すな
わち、前記トリクロロエチレンあるいは1,1,1−ト
リクロロエタンを含む空気を、通路を有する紫外線照射
装置3中を通過させて185nmの波長を含む低圧水銀
ランプ2(前記QGL25W−3)により紫外線を照射
し、ジクロロ酢酸等の親水化した有機塩素化合物に分解
したガスを生物処理装置4の下部に導入する。生物処理
装置4中には、微生物を保持させた充填材を充填した充
填相5が設けられており、生物処理装置4の底部の受水
槽に補給された補給水8を循環水7として充填相5の上
部の散水部から散水して充填相5を湿潤状態に維持す
る。前記生物処理装置4の下部に導入した前記親水化し
た有機塩素化合物を、充填相5内を通過させることによ
り、生物処理する。生物処理されたガスは生物処理装置
4の上部より流出ガス6として系外に排出する。
Example 1 The air containing 100 ppm of trichloroethylene and 30 ppm of 1,1,1-trichloroethane was treated using the apparatus shown in FIG. It processed on the processing conditions shown. That is, the air containing trichloroethylene or 1,1,1-trichloroethane is passed through an ultraviolet irradiation device 3 having a passage, and ultraviolet rays are irradiated by a low pressure mercury lamp 2 (the QGL25W-3) having a wavelength of 185 nm, A gas decomposed into a hydrophilized organic chlorine compound such as dichloroacetic acid is introduced into the lower part of the biological treatment apparatus 4. The biological treatment device 4 is provided with a filling phase 5 filled with a filler that holds microorganisms, and the makeup water 8 replenished in the water receiving tank at the bottom of the biological treatment device 4 is used as the circulating water 7. Water is sprayed from the water sprinkling part on the upper part of 5 to maintain the packed phase 5 in a wet state. Biological treatment is carried out by passing the hydrophilized organochlorine compound introduced into the lower part of the biological treatment apparatus 4 through the packed phase 5. The bioprocessed gas is discharged out of the system as an outflow gas 6 from the upper part of the bioprocessing device 4.

【0010】比較例1 100ppmのトリクロロエチレン及び30ppmの
1,1,1−トリクロロエタンを含む空気を、図2に示
す紫外線照射装置を用い、第1表の比較例1に示す処理
条件で紫外線照射処理した。すなわち、前記トリクロロ
エチレンあるいは1,1,1−トリクロロエタンを含む
空気(流入ガス9)を、通路を有する紫外線照射装置1
0中を通過させて実施例1と同じ種類の複数の低圧水銀
ランプ11により紫外線を照射し流出ガス126として
系外に排出する。 比較例2 100ppmのトリクロロエチレン及び30ppmの
1,1,1−トリクロロエタンを含む空気を、図3に示
す生物処理装置14を用い、第1表の比較例2に示す処
理条件で生物処理した。すなわち、実施例1に記載した
生物処理装置4におけると同様に微生物を保持させた充
填材を充填した充填相15が生物処理装置14に設けら
れており、生物処理装置14の底部の受水槽に補給され
た補給水17を循環水18として充填相15の上部の散
水部から散水して充填相15を湿潤状態に維持する。生
物処理装置14の下部に導入した前記トリクロロエチレ
ンあるいは1,1,1−トリクロロエタンを含む空気
(流入ガス13)を、充填相15内を通過させることに
より、生物処理する。生物処理されたガスは生物処理装
置14の上部より流出ガス16として系外に排出する。
前記実施例1、比較例1及び比較例2の処理能力の比較
を第1表に示す。
Comparative Example 1 Air containing 100 ppm of trichloroethylene and 30 ppm of 1,1,1-trichloroethane was subjected to ultraviolet irradiation treatment under the treatment conditions shown in Comparative Example 1 of Table 1 using the ultraviolet irradiation apparatus shown in FIG. . That is, the ultraviolet irradiation device 1 having a passage for the air (inflow gas 9) containing the trichlorethylene or 1,1,1-trichloroethane
After passing through 0, ultraviolet rays are irradiated by a plurality of low-pressure mercury lamps 11 of the same type as in Example 1, and discharged as outflow gas 126 out of the system. Comparative Example 2 Air containing 100 ppm of trichlorethylene and 30 ppm of 1,1,1-trichloroethane was biologically treated under the treatment conditions shown in Comparative Example 2 of Table 1 using the biological treatment apparatus 14 shown in FIG. That is, as in the case of the biological treatment apparatus 4 described in Example 1, the biological treatment apparatus 14 is provided with the packing phase 15 filled with the packing material holding the microorganisms, and the biological treatment apparatus 14 has a water receiving tank at the bottom thereof. The supplied makeup water 17 is sprinkled as circulating water 18 from the sprinkler section above the filling phase 15 to maintain the filling phase 15 in a wet state. Air (inflow gas 13) containing the trichloroethylene or 1,1,1-trichloroethane introduced into the lower part of the biological treatment device 14 is passed through the filling phase 15 for biological treatment. The bioprocessed gas is discharged out of the system as an outflow gas 16 from the upper part of the bioprocessing device 14.
Table 1 shows a comparison of the processing capacities of Example 1, Comparative Example 1 and Comparative Example 2.

【0011】[0011]

【表1】 [Table 1]

【0012】また、前記実施例1及び比較例1で使用し
た紫外線ランプの仕様を第2表に、前記実施例1及び比
較例3で使用した生物処理装置の仕様を第3表に示し
た。
Table 2 shows the specifications of the ultraviolet lamps used in Example 1 and Comparative Example 1, and Table 3 shows the specifications of the biological treatment apparatus used in Examples 1 and 3 respectively.

【0013】[0013]

【表2】 [Table 2]

【0014】[0014]

【表3】 [Table 3]

【0015】運転開始1ヵ月後の処理成績を実施例1、
比較例1及び比較例2について第4表に示す。紫外線照
射と生物処理の組合せ処理方法(実施例1の方法)では
トリクロロエチレンは99%以上除去され、1,1,1
−トリクロロエタンも78%除去された。全有機炭素も
92%除去された。一方、紫外線照射単独処理方法(比
較例1の方法)ではトリクロロエチレンはほとんど除去
され、1,1,1−トリクロロエタンは77%除去され
た。全有機炭素は除去率70%であった。これは、トリ
クロロエチレン及び1,1,1−トリクロロエタンが完
全に分解されず、性質の異なる物質に変化したことを示
している。また、生物単独処理の処理方法(比較例2の
方法)ではトリクロロエチレン及び1,1,1−トリク
ロロエタンはほとんど除去されなかった。
The treatment results one month after the start of operation are shown in Example 1,
Table 4 shows Comparative Example 1 and Comparative Example 2. Trichloroethylene was removed by 99% or more by the combined treatment method of ultraviolet irradiation and biological treatment (the method of Example 1).
-Trichloroethane was also removed by 78%. Total organic carbon was also removed by 92%. On the other hand, almost only trichloroethylene was removed and 77% of 1,1,1-trichloroethane was removed by the ultraviolet irradiation alone treatment method (the method of Comparative Example 1). The removal rate of all organic carbon was 70%. This indicates that trichloroethylene and 1,1,1-trichloroethane were not completely decomposed and changed into substances having different properties. Further, trichlorethylene and 1,1,1-trichloroethane were hardly removed by the treatment method of the biological treatment alone (the method of Comparative Example 2).

【0016】[0016]

【表4】 [Table 4]

【0017】[0017]

【発明の効果】本発明の処理方法は、紫外線照射単独で
完全分解させる方法と比較すると、消費エネルギーが少
なくてすむ。有機塩素化合物濃度が低い場合、燃焼処理
方法と比べても消費エネルギーが少なくてすむ。また、
本発明の処理方法は、生物処理で必要とされている誘導
物質の必要性がなく、しかも分解能力が高いため装置を
小型化できる。
The treatment method of the present invention consumes less energy as compared with the method of completely decomposing only by irradiation of ultraviolet rays. When the concentration of the organic chlorine compound is low, the energy consumption is small compared with the combustion treatment method. Also,
Since the treatment method of the present invention does not require an inducer required for biological treatment and has a high decomposition ability, the apparatus can be downsized.

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

【図1】紫外線照射と生物処理の組合せ処理方法で行う
処理装置の例を示す概念図である。
FIG. 1 is a conceptual diagram showing an example of a processing apparatus that performs a combined processing method of ultraviolet irradiation and biological treatment.

【図2】紫外線照射単独の処理方法で行う処理装置の例
を示す概念図である。
FIG. 2 is a conceptual diagram showing an example of a processing device that performs a processing method of ultraviolet irradiation alone.

【図3】生物処理単独で行う処理装置の例を示す概念図
である。
FIG. 3 is a conceptual diagram showing an example of a processing apparatus that performs biological processing alone.

【符号の説明】[Explanation of symbols]

1 流入ガス 2 低圧水銀ランプ 3 紫外線照射装置 4 生物処理装置 5 充填相 6 流出ガス 7 循環水 8 補給水 9 流入ガス 10 紫外線照射装置 11 紫外線ランプ(低圧水銀ランプ) 12 流出ガス 13 流入ガス 14 生物処理装置 15 充填相 16 流出ガス 17 補給水 18 循環水 1 Inflow Gas 2 Low Pressure Mercury Lamp 3 Ultraviolet Irradiation Device 4 Biological Treatment Device 5 Filling Phase 6 Outflow Gas 7 Circulating Water 8 Makeup Water 9 Inflow Gas 10 Ultraviolet Irradiation Device 11 Ultraviolet Lamp (Low Pressure Mercury Lamp) 12 Outflow Gas 13 Inflow Gas 14 Biological Treatment device 15 Filling phase 16 Outflow gas 17 Make-up water 18 Circulating water

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 揮発性有機塩素化合物を含む排ガスに対
して紫外線を照射し、該揮発性有機塩素化合物の物性を
変化させる工程と、続いて微生物を湿潤状態で保持した
充填材を充填した生物処理装置を通過させて処理する工
程を有することを特徴とする揮発性有機塩素化合物を含
む排ガスの処理方法。
1. A step of irradiating an exhaust gas containing a volatile organochlorine compound with ultraviolet rays to change the physical properties of the volatile organochlorine compound, and subsequently, a living organism filled with a filler that keeps microorganisms in a wet state. A method for treating an exhaust gas containing a volatile organic chlorine compound, comprising the step of passing the treatment through a treatment device.
【請求項2】 揮発性有機塩素化合物を含む排ガスに対
して紫外線を照射する照射装置と、充填塔内に微生物を
保持できる充填材を設け、該充填材の上部に散水部を配
備すると共に、充填塔下部に受水槽を配備し、該充填材
を湿潤状態に維持した生物処理装置とを有し、順次前記
紫外線照射装置と、前記生物処理装置とに前記排ガスを
通過させて処理するよう配置することを特徴とする揮発
性有機塩素化合物を含む排ガスの処理装置。
2. An irradiation device for irradiating an exhaust gas containing a volatile organic chlorine compound with ultraviolet rays, a packing material capable of holding microorganisms in a packed tower, and a sprinkler section provided on the packing material. A water receiving tank is provided in the lower part of the packed tower, and a biological treatment device in which the packing material is maintained in a wet state is provided, and the ultraviolet irradiation device and the biological treatment device are sequentially arranged to pass the exhaust gas for treatment. An apparatus for treating exhaust gas containing a volatile organic chlorine compound, which is characterized by:
JP7115245A 1995-04-18 1995-04-18 Treatment of waste gases containing volatile organic chlorine compound and treating device therefor Withdrawn JPH08281066A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7115245A JPH08281066A (en) 1995-04-18 1995-04-18 Treatment of waste gases containing volatile organic chlorine compound and treating device therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7115245A JPH08281066A (en) 1995-04-18 1995-04-18 Treatment of waste gases containing volatile organic chlorine compound and treating device therefor

Publications (1)

Publication Number Publication Date
JPH08281066A true JPH08281066A (en) 1996-10-29

Family

ID=14657941

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7115245A Withdrawn JPH08281066A (en) 1995-04-18 1995-04-18 Treatment of waste gases containing volatile organic chlorine compound and treating device therefor

Country Status (1)

Country Link
JP (1) JPH08281066A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6632659B1 (en) * 1999-09-10 2003-10-14 S.M. Sze Apparatus and method for UV oxidation and microbiological decomposition of organic waste air

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6632659B1 (en) * 1999-09-10 2003-10-14 S.M. Sze Apparatus and method for UV oxidation and microbiological decomposition of organic waste air

Similar Documents

Publication Publication Date Title
JPH05228480A (en) Device for processing hardly biodegradable substance
KR20080057808A (en) Odor gas treatment device having biochemical odor gas treatment unit
JP2008036513A (en) Unit and system for gas treatment
JPH05228481A (en) Device for processing hardly biodegradable substance
JPH05228496A (en) Method for processing hardly biodegradable substance
EP1491218A1 (en) Illuminator capable of cleaning air
JP3476293B2 (en) Odor gas deodorizing method and apparatus
JPH08281066A (en) Treatment of waste gases containing volatile organic chlorine compound and treating device therefor
CN110252127A (en) A kind of petrochemical industry exhaust treatment system
JPS6348567B2 (en)
EP0242941B1 (en) Process and apparatus for the deodorization of air
KR100239241B1 (en) Deodorizing method and its apparatus with optical catalyst
JPH09234338A (en) Photolysis of organochlorine compound
JPH1110136A (en) Process and device for water treatment
JP2008141986A (en) Apparatus for treating tank water for fish, and method for treating tank water for fish
JPH08281068A (en) Treatment of waste gases containing volatile organic matter and treating device therefor
KR100928839B1 (en) Recycling hybrid system combined with photocatalytic reactor, biofilter and nitrification / denitrification reactor
JPH01218676A (en) Method for treating waste water
JPH07155543A (en) Treatment for volatile organic chlorine compound and device therefor
JP2002018240A (en) Method and apparatus for treatment for rendering hazardous organic substance harmless
KR100954751B1 (en) Devices for the treatment of waste air containing malodor and VOCs
JP3144302B2 (en) Fluid treatment equipment
JPH06134315A (en) Catalyst for reduction treatment of volatile organic halogen compound
JPH09299753A (en) Organic chlorine compound photolysis device
JP2001104996A (en) Water treatment method and apparatus

Legal Events

Date Code Title Description
A761 Written withdrawal of application

Free format text: JAPANESE INTERMEDIATE CODE: A761

Effective date: 20031226

A761 Written withdrawal of application

Free format text: JAPANESE INTERMEDIATE CODE: A761

Effective date: 20040122

A072 Dismissal of procedure

Free format text: JAPANESE INTERMEDIATE CODE: A073

Effective date: 20040317