JPS60114328A - Treatment of gas containing hydrogen arsenide - Google Patents

Treatment of gas containing hydrogen arsenide

Info

Publication number
JPS60114328A
JPS60114328A JP58219376A JP21937683A JPS60114328A JP S60114328 A JPS60114328 A JP S60114328A JP 58219376 A JP58219376 A JP 58219376A JP 21937683 A JP21937683 A JP 21937683A JP S60114328 A JPS60114328 A JP S60114328A
Authority
JP
Japan
Prior art keywords
gas
ash3
hydrogen arsenide
adsorbent
gas containing
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
Application number
JP58219376A
Other languages
Japanese (ja)
Other versions
JPS629367B2 (en
Inventor
Izuru Nagatani
永谷 出瑠
Hisamatsu Mizuno
久松 水野
Toshinobu Mitsui
三井 利▲のぶ▼
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.)
Showa Engineering Co Ltd
Resonac Holdings Corp
Original Assignee
Showa Denko KK
Showa Engineering 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 Showa Denko KK, Showa Engineering Co Ltd filed Critical Showa Denko KK
Priority to JP58219376A priority Critical patent/JPS60114328A/en
Publication of JPS60114328A publication Critical patent/JPS60114328A/en
Publication of JPS629367B2 publication Critical patent/JPS629367B2/ja
Granted legal-status Critical Current

Links

Abstract

PURPOSE:To treat the titled gas by a dry process being a simple process with the usage of an easily obtainable adsorbent by passing a gas containing AsH3 through a packed layer of bleaching powder or the mixture of bleaching powder, iron compound, and diatom earth after humidifying the gas and by oxidizing and adsorbing the AsH3. CONSTITUTION:An adsorbent consisting of simple high test hypochlorite Ca(OCl)2 or the mixture of hypochlorite, iron compound such as FeCl3, and diatom earth is packed into a packed layer. After humidifying a gas containing AsH3 by bubbling the gas in water or a spraying nozzle, etc., the gas is passed through the packed layer. The AsH3 contained in the gas is oxidized and adsorbed by the adsorbent.

Description

【発明の詳細な説明】 この発明は一半導体電子工業の半導体及び集積回路の製
造工程において砒化水素、リン化水素等の金属水素化物
をドーピングガスとして用いられているが、その工程又
は他の化学工業から排出される砒化水素含有ガスを乾式
によって処理する方法に関する。
Detailed Description of the Invention This invention relates to the use of metal hydrides such as hydrogen arsenide and hydrogen phosphide as doping gases in the manufacturing process of semiconductors and integrated circuits in the semiconductor electronics industry. This invention relates to a method for dry processing of hydrogen arsenide-containing gas discharged from industry.

砒化水素(アルシン・AsH3)やリン化水素(ホスフ
ィン・PHa )等は毒性が強く、工程からこれら有毒
ガスが無処理のまま大気中へ放散させると人体の健康に
非常に悪影響をおよぼし、最悪の場合には生命に危険を
生せしめる虞れがあるために、当然に無害化処理が必要
となる。
Hydrogen arsenide (Arsine/AsH3) and hydrogen phosphide (phosphine/PHa) are highly toxic, and if these toxic gases are released into the atmosphere from the process without being treated, they will have a very negative impact on human health, resulting in the worst In some cases, there is a possibility that it may pose a danger to life, so it is naturally necessary to detoxify it.

現在、半導体電子工業あるいは他の化学工業で排出され
るヒ化水素を含有する排ガスの処理方法として採用され
ている方法を大別すると、固体吸着法、過マンガン酸カ
リ酸化吸収法、燃焼分解法が提案されている。
Currently, the methods used to treat exhaust gas containing hydrogen arsenide emitted by the semiconductor electronics industry or other chemical industries can be roughly divided into solid adsorption methods, potassium permanganate oxidation and absorption methods, and combustion decomposition methods. is proposed.

これらの処理方法の概要は次のとおりである固体吸着法
の代表例は、特公昭58−34178号公報に見られる
ように、「塩化第二鉄を主材に水酸化第二鉄、塩化第二
銅、酸化第二銅、塩化マグネシウム及び塩化第二水銀を
助材として加え、これに水を加えた溶液剤を多孔性物質
に浸透・させて成る浄化剤組成物」を使用して排ガスを
浄化する方法であり、その浄化原理は同公報の詳細な説
明中に、AsHa+5FeC13+4(20−+ 6F
eC12+6HC1+H3As03 (1) 3MCI+Fe(OH)3−+FeCIa+3H20(
2)の吸収機構と再生機構よりなっている。この方法に
おいて、助材として塩化第二水銀を用いるとHgが処理
廃水、処理廃棄物中に含まれ、その処理が問題となる。
The outline of these treatment methods is as follows.A typical example of the solid adsorption method is as seen in Japanese Patent Publication No. 58-34178. Exhaust gas is purified by using a purifying agent composition in which a porous material is infiltrated with a solution prepared by adding cupric oxide, cupric oxide, magnesium chloride, and mercuric chloride as auxiliary materials and water. This purification method is described in detail in the same publication as AsHa+5FeC13+4(20-+6F
eC12+6HC1+H3As03 (1) 3MCI+Fe(OH)3-+FeCIa+3H20(
It consists of an absorption mechanism and a regeneration mechanism (2). In this method, when mercuric chloride is used as an auxiliary material, Hg is contained in the treated wastewater and treated waste, and its treatment becomes a problem.

過マンガン酸力!J (KMnOa)酸化吸収法は、K
MnO4水溶液を吸収剤どし、次式の反応式に従って吸
収除去する方法である。
Permanganese acid power! J (KMnOa) oxidation absorption method
This is a method in which an aqueous MnO4 solution is passed through an absorbent and absorbed and removed according to the following reaction formula.

AsH3+2KMnO4→KzHAs04+Mn 20
3+H20この方法においては、酸化マンガンが生成さ
れて、吸収装置内への沈積による閉塞等に問題がある。
AsH3+2KMnO4→KzHAs04+Mn 20
3+H20 In this method, manganese oxide is produced and there are problems such as clogging due to deposition in the absorption device.

燃焼分解法は、3000程度でASH3を酸化分解させ
る方法であって、運転管理が煩雑にしてコスト高となる
問題がある。
The combustion decomposition method is a method in which ASH3 is oxidized and decomposed at about 3000 ml, and has the problem of complicated operation management and high cost.

上記各処理方法については、夫々一長一短があり、技術
性及び経済性は一般に正当化されない傾向がある。
Each of the above processing methods has its own advantages and disadvantages, and generally tends not to be justified in terms of technical efficiency and economic efficiency.

この発明は、運転管理が容易にして入手容易な吸着剤を
使用して処理コストの低減を図り、しかも処理廃棄物等
に有害物質を含有せしめず(3) 二次薬害の処理等の問題も少ない砒化水素含有ガスの処
理方法を提供する目的をもって開発したものである。
This invention aims to reduce treatment costs by using adsorbents that are easy to operate and obtain, and does not contain harmful substances in treated waste. (3) Problems such as treatment of secondary chemical damage are avoided It was developed with the aim of providing a method for processing gas containing a small amount of hydrogen arsenide.

この発明の特徴は、砒化水素含有ガスを増湿して後、さ
らし粉の単味もしくはこのものと鉄化合物、ケイソウ土
との混合物より成る吸着剤の充填層に流通せしめてガス
中の砒化水素を酸化吸着させることにある。
The feature of this invention is that after the hydrogen arsenide-containing gas is humidified, it is passed through a packed bed of an adsorbent made of bleaching powder alone or a mixture of this powder and an iron compound or diatomaceous earth to remove hydrogen arsenide from the gas. The purpose is to oxidize and adsorb it.

高度晒粉の主成分は1次亜塩素酸カルシウム(Ca(O
CI )2)であり1通常の晒粉(CaOCI2)より
も有効塩素の量が多いのでAsH3の処理に好ましいが
、通常の晒粉も必要に応じて使用することができる。こ
のことは晒粉の主要成分は塩化カルシウムと次亜塩素酸
カルシウムとの混合塩であるとされているからである。
The main component of highly bleached powder is primary calcium hypochlorite (Ca(O
CI)2) 1 It is preferable for the treatment of AsH3 because it has a larger amount of available chlorine than normal bleached powder (CaOCI2), but normal bleached powder can also be used if necessary. This is because the main component of bleached powder is said to be a mixed salt of calcium chloride and calcium hypochlorite.

この発明で述べられる鉄化合物は、生成されたAsを捕
集して系外へ溶出させない目的で添加するものであり一
酸化鉄(Fe 203 )や塩化第二鉄(FeCl3)
が用いられる〇 ケイソウ土は加湿によって吸着剤が泥土化す(A’+ ることを防止するために添加される。ケイソウ土の添加
量は晒粉量に対して、2〜4倍量が用いられる。また鉄
化合物の添加量は晒粉のし2〜174量が添加される。
The iron compounds mentioned in this invention are added to collect the generated As and prevent it from eluting out of the system, and include iron monoxide (Fe203) and ferric chloride (FeCl3).
〇Diatomaceous earth is added to prevent the adsorbent from turning into mud due to humidification (A'+).The amount of diatomaceous earth added is 2 to 4 times the amount of bleaching powder. Further, the amount of iron compound added is 2 to 174 times the amount of bleached powder.

砒化水素含有ガスは予め増湿することによって晒粉の酸
化効率を高めることができる。増湿操作は水中へのバブ
リング、噴霧ノズル等による方式などが採用される。ど
の位に増湿するかは、吸着剤の充填量やガス中の砒化水
素濃度などの処理条件を考慮して定められる。
The oxidation efficiency of bleached powder can be increased by humidifying the hydrogen arsenide-containing gas in advance. Humidification operations include bubbling into the water, spray nozzles, and other methods. The degree to which the humidity is increased is determined by considering processing conditions such as the amount of adsorbent packed and the hydrogen arsenide concentration in the gas.

次にこの発明の実施例を示す。Next, examples of this invention will be shown.

実施例ま た 水150m7を容れ9シリンダーに砒化水素含有ガス(
AsH31ppm、湿度0係、温度25C)を導入し、
バブリングさせた後、15 mmグX 150mm)(
の吸着塔に、高度晒粉(有効塩素60%) 4g、 F
eCl31g、ケイソウ±10gの混合物(15g)を
充填した充填層に、流通ガス量2.4 l/Hrで夫々
流通した。充填層入口のガス中の湿度は温度25Cにお
いて夫々0%、65係であった。実施(tk) の結果を図表化して添付図に示した。
Example: Hydrogen arsenide-containing gas (
Introducing AsH31ppm, humidity 0, temperature 25C),
After bubbling, 15 mm × 150 mm) (
4g of highly bleached powder (available chlorine 60%), F
The gas was passed through a packed bed filled with a mixture (15 g) of 31 g of eCl and ±10 g of diatomaceous material at a flow rate of 2.4 l/Hr. The humidity in the gas at the inlet of the packed bed was 0% and 65% at a temperature of 25C, respectively. The results of the implementation (tk) are shown in the attached figure.

同図が示すように、砒化水素含有ガスを増湿することに
よって、処理ガス中の砒化水素濃度を0.O5ppm以
下にすることができた。
As shown in the figure, by humidifying the hydrogen arsenide-containing gas, the hydrogen arsenide concentration in the treated gas can be reduced to 0. We were able to reduce the O to 5 ppm or less.

実施例2 Ca(CIO) 2の砒素吸着性能を知見するために。Example 2 To understand the arsenic adsorption performance of Ca(CIO)2.

砒素発生器(Asia +Zn +KI )で砒素を発
生し、導入空気に同伴(湿度67%一温度26C)させ
て、15mmm x 150+u+Hの吸着塔に高度晒
粉(有効塩素60%)10gを充填した充填層に2 l
/Hrの流通量で流通し、排出ガスをジエチルヂチオカ
ルバミン酸銀液を容れたシリンダー中の同液に流通し、
 Asの濃度を測定したところ次表の結果を得たこの発
明の方法に従えば、湿式法に比較してプロセスが単純化
されるので、運転管理が非常に容易となると共に有害物
が処理廃棄物等に混入しないので二次処理に問題が少な
く、しかも入手容易な吸着剤を使用すると共にユテイリ
テイの消費量も少ないので処理コストの低減が図られる
等の利益をもたらす。
Arsenic was generated in an arsenic generator (Asia + Zn + KI) and entrained in the introduced air (humidity 67% - temperature 26C), and a 15mm x 150+U+H adsorption tower was filled with 10g of highly bleached powder (available chlorine 60%). 2 l in layer
/Hr, and the exhaust gas is distributed to a cylinder containing a silver diethyldithiocarbamate solution,
When the concentration of As was measured, the results shown in the table below were obtained. If the method of this invention is followed, the process is simplified compared to the wet method, so operation management is extremely easy, and hazardous substances are processed and disposed of. Since it does not mix with materials, there are few problems in secondary processing, and since an easily available adsorbent is used and the amount of utility consumed is small, it brings benefits such as a reduction in processing costs.

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

図面はこの発明の実施例の結果を図表化した図表である
。 (7) 出口ガス 流通ガスICI/Hr)
The drawings are diagrams illustrating the results of the embodiments of the present invention. (7) Outlet gas distribution gas ICI/Hr)

Claims (1)

【特許請求の範囲】[Claims] 砒化水素含有ガスを増湿して後、さらし粉の単味もしく
はこのものと鉄化合物、ケイソウ土との混合物よりなる
吸着剤の充填層に流通せしめてガス中の砒化水素を酸化
吸着させることを特徴とする砒化水素含有ガスの処理方
法。
The feature is that after humidifying the hydrogen arsenide-containing gas, it is passed through a packed bed of an adsorbent made of bleaching powder alone or a mixture of this powder and an iron compound or diatomaceous earth to oxidize and adsorb the hydrogen arsenide in the gas. A method for treating hydrogen arsenide-containing gas.
JP58219376A 1983-11-24 1983-11-24 Treatment of gas containing hydrogen arsenide Granted JPS60114328A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58219376A JPS60114328A (en) 1983-11-24 1983-11-24 Treatment of gas containing hydrogen arsenide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58219376A JPS60114328A (en) 1983-11-24 1983-11-24 Treatment of gas containing hydrogen arsenide

Publications (2)

Publication Number Publication Date
JPS60114328A true JPS60114328A (en) 1985-06-20
JPS629367B2 JPS629367B2 (en) 1987-02-27

Family

ID=16734445

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58219376A Granted JPS60114328A (en) 1983-11-24 1983-11-24 Treatment of gas containing hydrogen arsenide

Country Status (1)

Country Link
JP (1) JPS60114328A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4869735A (en) * 1987-04-30 1989-09-26 Mitsubishi Jukogyo K.K. Adsorbent for arsenic compound and method for removing arsenic compound from combustion gas

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0472558U (en) * 1990-11-02 1992-06-25

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5095104A (en) * 1973-12-26 1975-07-29
JPS58122026A (en) * 1982-01-13 1983-07-20 Mitsubishi Rayon Co Ltd Removal of arsenic component in gas

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5095104A (en) * 1973-12-26 1975-07-29
JPS58122026A (en) * 1982-01-13 1983-07-20 Mitsubishi Rayon Co Ltd Removal of arsenic component in gas

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4869735A (en) * 1987-04-30 1989-09-26 Mitsubishi Jukogyo K.K. Adsorbent for arsenic compound and method for removing arsenic compound from combustion gas

Also Published As

Publication number Publication date
JPS629367B2 (en) 1987-02-27

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