JPH06182151A - Treatment of exhaust gas - Google Patents
Treatment of exhaust gasInfo
- Publication number
- JPH06182151A JPH06182151A JP4339936A JP33993692A JPH06182151A JP H06182151 A JPH06182151 A JP H06182151A JP 4339936 A JP4339936 A JP 4339936A JP 33993692 A JP33993692 A JP 33993692A JP H06182151 A JPH06182151 A JP H06182151A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- methane
- chlorine derivatives
- gas containing
- ethylene
- 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.)
- Granted
Links
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明はメタンの塩素誘導体を含
んだ排ガスの処理方法に関する。FIELD OF THE INVENTION The present invention relates to a method for treating exhaust gas containing a chlorine derivative of methane.
【0002】[0002]
【従来の技術】基板洗浄ライン等より排出されるトリク
ロロエチレン、テトラクロロエチレン、1,1,1−ト
リクロロエタン、四塩化炭素、クロロホルム、ジクロロ
メタン等の有害な揮発性有機塩素化合物を含有する排水
は、ばっ気して大気中に未処理のまま放出されているの
が現状であり、地球環境保全上問題があった。2. Description of the Related Art Wastewater containing harmful volatile organic chlorine compounds such as trichloroethylene, tetrachloroethylene, 1,1,1-trichloroethane, carbon tetrachloride, chloroform and dichloromethane discharged from a substrate cleaning line is aeration. At present, it is released into the atmosphere as untreated, which is a problem in terms of global environmental protection.
【0003】[0003]
【発明が解決しようとする課題】上記問題点を解決する
ための手段として、本発明者は既に「排ガス処理装置」
(実願平2〜110500号)を初め、種々の技術を提
案している。これらの内容は波長184.9nmの紫外
線(UV)と紫外線により生成された発生期のオゾン
(O3 )、あるいは光触媒によって排ガス中に含まれる
揮発性有機塩素化合物を無機化合物に分解し、さらにオ
ゾン分解触媒により残留オゾンを酸素に分解して無害化
する方法である。しかしながら、四塩化炭素、クロロホ
ルム、ジクロロメタン等のメタンの塩素誘導体は紫外線
照射やオゾン並びに光触媒下では容易に分解しないとい
う問題があった。As a means for solving the above problems, the present inventor has already proposed "exhaust gas treatment device".
Various techniques have been proposed including (Japanese Patent Application No. 2-110500). These contents are ultraviolet rays (UV) having a wavelength of 184.9 nm and nascent ozone (O 3 ) generated by the ultraviolet rays, or a photocatalyst decomposes a volatile organic chlorine compound contained in exhaust gas into an inorganic compound, and further ozone This is a method of decomposing residual ozone into oxygen by a decomposition catalyst to make it harmless. However, there is a problem that chlorine derivatives of methane such as carbon tetrachloride, chloroform and dichloromethane are not easily decomposed under irradiation of ultraviolet rays, ozone and a photocatalyst.
【0004】本発明は上記技術水準に鑑み、容易に分解
しないメタンの塩素誘導体を含む排ガス無害化するため
の処理方法を提供しようとするものである。In view of the above-mentioned state of the art, the present invention is to provide a treatment method for detoxifying an exhaust gas containing a chlorine derivative of methane which is not easily decomposed.
【0005】[0005]
【課題を解決するための手段】本発明はメタンの塩素誘
導体を含む排ガス中にガス状のエチレンの塩素誘導体を
少量加えた後、該ガスに紫外線を照射することを特徴と
するメタンの塩素誘導体を含む排ガスの処理方法であ
る。The present invention is characterized in that a small amount of a gaseous chlorine derivative of ethylene is added to an exhaust gas containing a chlorine derivative of methane, and then the gas is irradiated with ultraviolet rays. It is a method of treating exhaust gas containing.
【0006】本発明でいうメタンの塩素誘導体とは四塩
化炭素、クロロホルム、ジクロロメタン、クロロメタン
などであり、エチレンの塩素誘導体とはトリクロロエチ
レン、テトラクロロエチレンなどである。The chlorine derivative of methane in the present invention means carbon tetrachloride, chloroform, dichloromethane, chloromethane and the like, and the chlorine derivative of ethylene means trichloroethylene, tetrachloroethylene and the like.
【0007】[0007]
【作用】有機塩素化合物は紫外線を照射することにより
二酸化炭素(CO2 )と塩化水素ガス(HCl)に分解
されることが知られている。{今川 隆,化学工業 4
1,(1) 24〜27 '90,久永輝明,原田賢二等 水処理技
術 29,(8)483〜487 '88}また、一般にメタンの誘導
体はエチレンの誘導体より分解しにくく、かつ炭素数が
同じ場合には置換塩素の数が多いほど分解しにくいこと
もよく知られていることである。(久永輝明,原田賢二
等,工技院レポート '89)It is known that an organic chlorine compound is decomposed into carbon dioxide (CO 2 ) and hydrogen chloride gas (HCl) by irradiating it with ultraviolet rays. {Takashi Imagawa, Chemical Industry 4
1 , (1) 24-27 '90, Teruaki Kuninaga, Kenji Harada, etc. Water treatment technology 29 , (8) 483-487 '88} Generally, methane derivatives are more difficult to decompose than ethylene derivatives and have carbon numbers. In the same case, it is well known that the larger the number of substituted chlorines, the more difficult it is to decompose. (Teraki Kuninaga, Kenji Harada, Institute of Technology Report '89)
【0008】例えば、トリクロロエチレン(C2 HCl
3 )の紫外線(UV)による分解反応は次のようであ
り、ラジカルを経て分解される。For example, trichlorethylene (C 2 HCl
The decomposition reaction of 3 ) by ultraviolet rays (UV) is as follows, and is decomposed via radicals.
【0009】[0009]
【化1】 [Chemical 1]
【0010】一方、メタンの塩素誘導体は紫外線の照射
のみでは同様なラジカルを生成しにくいため分解しにく
い。そこで、難分解性有機塩素化合物を含む排ガスの中
に紫外線照射により分解しやすい物質を少量加え、これ
を分解させることにより(1)式で生じたH・ラジカル
が下記(3)式に示すようにO3 の分解時に発生する発
生期の酸素(O* )あるいは(4)式に示すようにH2
Oと反応して強い酸化力をもつ・OHラジカルに変換す
る。この・OHラジカルがメタンの塩素誘導体を酸化分
解することにより、下記(5)式,(6)式に示すよう
に紫外線照射のみでは分解されにくいジクロロメタンの
如きメタンの塩素誘導体も容易に分解される。すなわち
トリクロロエチレンはラジカル分解反応の開始剤として
作用する。一度・OHラジカルが生成された後は(4)
式に示すように1個のH・ラジカルから2個のH・ラジ
カルが生成するので連鎖反応により瞬時に分解が進行
し、短時間で高い分解率が得られることになる。On the other hand, the chlorine derivative of methane is hard to generate similar radicals only by irradiation with ultraviolet rays, and is therefore difficult to decompose. Therefore, a small amount of a substance that is easily decomposed by ultraviolet irradiation is added to the exhaust gas containing the hardly decomposable organochlorine compound, and the H · radical generated in the formula (1) is generated as shown in the formula (3) below. Of oxygen (O * ) generated during decomposition of O 3 or H 2 as shown in equation (4).
Reacts with O and has strong oxidizing power. By this OH radical oxidatively decomposing a chlorine derivative of methane, a chlorine derivative of methane such as dichloromethane, which is difficult to be decomposed only by UV irradiation, is easily decomposed as shown in the following formulas (5) and (6). . That is, trichlorethylene acts as an initiator of radical decomposition reaction. Once the OH radical is generated (4)
As shown in the formula, since two H · radicals are produced from one H · radical, the chain reaction instantaneously decomposes, and a high decomposition rate can be obtained in a short time.
【0011】[0011]
【化2】 [Chemical 2]
【0012】[0012]
【実施例】本発明の一実施態様としての試験装置の構成
を図1に従って詳述する。図1において、テドラーバッ
グ1内で所定濃度に調整された排ガスをポンプ2で光分
解反応器4に所定流量で流す。3は光分解反応器4に所
定(一定)量で流すためのバッファタンクである。光分
解反応器4内に設置したHgランプ5から紫外線を発生
させ排ガス中の有機塩素化合物を分解する。分解率はサ
ンプリング点6及びサンプリング点7から排ガスを採取
しFID検出器付きのガスクロマトグラフで濃度を分析
して算出する。紫外線発生時に副生するオゾンが排ガス
中に残存すると分析中(ガスクロマトグラフによる分
析)に有機塩素化合物と反応して有機塩素化合物濃度が
低くなり、排ガス中の濃度を正しく分析することができ
なくなるため、事前にハイポ溶液などでオゾンを吸収す
る。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The configuration of a test apparatus as an embodiment of the present invention will be described in detail with reference to FIG. In FIG. 1, the exhaust gas adjusted to have a predetermined concentration in the Tedlar bag 1 is caused to flow by the pump 2 into the photolysis reactor 4 at a predetermined flow rate. Reference numeral 3 is a buffer tank for flowing a predetermined (constant) amount into the photolysis reactor 4. Ultraviolet rays are generated from the Hg lamp 5 installed in the photolysis reactor 4 to decompose the organic chlorine compound in the exhaust gas. The decomposition rate is calculated by collecting exhaust gas from sampling points 6 and 7 and analyzing the concentration with a gas chromatograph equipped with an FID detector. If ozone, which is a by-product of the generation of ultraviolet rays, remains in the exhaust gas, it reacts with the organic chlorine compound during analysis (analysis by gas chromatograph) and the concentration of the organic chlorine compound decreases, making it impossible to accurately analyze the concentration in the exhaust gas. In advance, absorb ozone with hypo solution.
【0013】(実験例)100ppmあるいは1000
ppmに調整したメタンの塩素誘導体及び1ppmある
いは10ppmに調整したエチレンの塩素誘導体を含む
排ガスに184.9nmの紫外線を含む紫外線を発生さ
せるHgランプを照射した結果を表1に示す。メタンの
塩素誘導体のみでは分解しにくいのに比べてエチレンの
塩素誘導体を微量共存させることにより大巾な分解率の
向上が見られる。(Experimental example) 100 ppm or 1000
Table 1 shows the results obtained by irradiating the exhaust gas containing the chlorine derivative of methane adjusted to ppm and the chlorine derivative of ethylene adjusted to 1 ppm or 10 ppm with an Hg lamp for generating ultraviolet rays containing ultraviolet rays of 184.9 nm. In contrast to the difficulty of decomposing only with the chlorine derivative of methane, a significant improvement in the decomposition rate can be seen by coexisting with a minute amount of the chlorine derivative of ethylene.
【0014】[0014]
【表1】 [Table 1]
【0015】[0015]
【発明の効果】紫外線の照射及び紫外線照射時に副生す
るオゾンの作用並びに光触媒によっても分解しにくいメ
タンの塩素誘導体を含む排ガスの中に、エチレンの塩素
誘導体を微量加えることでメタンの塩素誘導体を迅速
に、かつ高効率に無機化合物に分解し、外部へ排出され
るガスを無害化するので、地球環境保全に役立つ。The chlorine derivative of methane can be obtained by adding a trace amount of the chlorine derivative of ethylene to the exhaust gas containing the chlorine derivative of methane which is difficult to be decomposed by the action of ozone and by-product of ultraviolet irradiation and the photocatalyst. It quickly and highly efficiently decomposes into inorganic compounds and detoxifies the gas discharged to the outside, which is useful for global environment conservation.
【図1】本発明の一実施態様としての試験装置の構成
図。FIG. 1 is a configuration diagram of a test apparatus as an embodiment of the present invention.
Claims (1)
ス状のエチレンの塩素誘導体を少量加えた後、該ガスに
紫外線を照射することを特徴とするメタンの塩素誘導体
を含む排ガスの処理方法。1. A method for treating an exhaust gas containing a chlorine derivative of methane, which comprises adding a small amount of a gaseous chlorine derivative of ethylene to an exhaust gas containing the chlorine derivative of methane and then irradiating the gas with ultraviolet rays.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4339936A JP2809367B2 (en) | 1992-12-21 | 1992-12-21 | Exhaust gas treatment method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4339936A JP2809367B2 (en) | 1992-12-21 | 1992-12-21 | Exhaust gas treatment method |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH06182151A true JPH06182151A (en) | 1994-07-05 |
JP2809367B2 JP2809367B2 (en) | 1998-10-08 |
Family
ID=18332165
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP4339936A Expired - Fee Related JP2809367B2 (en) | 1992-12-21 | 1992-12-21 | Exhaust gas treatment method |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2809367B2 (en) |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP1010453A1 (en) * | 1998-12-16 | 2000-06-21 | Canon Kabushiki Kaisha | Method and apparatus for decomposing gaseous aliphatic hydrocarbon halide compound |
EP1163946A1 (en) * | 2000-06-16 | 2001-12-19 | Canon Kabushiki Kaisha | Process and system for decomposing pollutants |
US6616815B2 (en) | 1998-06-22 | 2003-09-09 | Canon Kabushiki Kaisha | Method of decomposing halogenated aliphatic hydrocarbon compounds or aromatic compounds and apparatus to be used for the same as well as method of clarifying exhaust gas and apparatus to be used for the same |
US7018514B2 (en) | 2001-11-12 | 2006-03-28 | Canon Kabushiki Kaisha | Method and apparatus for processing substances to be decomposed |
US7163615B2 (en) | 2001-11-12 | 2007-01-16 | Canon Kabushiki Kaisha | Method of treating substance to be degraded and its apparatus |
-
1992
- 1992-12-21 JP JP4339936A patent/JP2809367B2/en not_active Expired - Fee Related
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6616815B2 (en) | 1998-06-22 | 2003-09-09 | Canon Kabushiki Kaisha | Method of decomposing halogenated aliphatic hydrocarbon compounds or aromatic compounds and apparatus to be used for the same as well as method of clarifying exhaust gas and apparatus to be used for the same |
EP1010453A1 (en) * | 1998-12-16 | 2000-06-21 | Canon Kabushiki Kaisha | Method and apparatus for decomposing gaseous aliphatic hydrocarbon halide compound |
US6497795B1 (en) | 1998-12-16 | 2002-12-24 | Canon Kabushiki Kaisha | Method and apparatus for decomposing gaseous aliphatic hydrocarbon halide compound |
US7163665B2 (en) | 1998-12-16 | 2007-01-16 | Canon Kabushiki Kaisha | Apparatus for decomposing gaseous aliphatic hydrocarbon halide compounds |
EP1163946A1 (en) * | 2000-06-16 | 2001-12-19 | Canon Kabushiki Kaisha | Process and system for decomposing pollutants |
US6699370B2 (en) | 2000-06-16 | 2004-03-02 | Canon Kabushiki Kaisha | Process and system for decomposing pollutants |
US7018514B2 (en) | 2001-11-12 | 2006-03-28 | Canon Kabushiki Kaisha | Method and apparatus for processing substances to be decomposed |
US7163615B2 (en) | 2001-11-12 | 2007-01-16 | Canon Kabushiki Kaisha | Method of treating substance to be degraded and its apparatus |
Also Published As
Publication number | Publication date |
---|---|
JP2809367B2 (en) | 1998-10-08 |
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Legal Events
Date | Code | Title | Description |
---|---|---|---|
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 19980623 |
|
LAPS | Cancellation because of no payment of annual fees |