JPH10216479A - Detoxifying method of gaseous nitrogen trifluoride - Google Patents

Detoxifying method of gaseous nitrogen trifluoride

Info

Publication number
JPH10216479A
JPH10216479A JP9018755A JP1875597A JPH10216479A JP H10216479 A JPH10216479 A JP H10216479A JP 9018755 A JP9018755 A JP 9018755A JP 1875597 A JP1875597 A JP 1875597A JP H10216479 A JPH10216479 A JP H10216479A
Authority
JP
Japan
Prior art keywords
gas
catalyst
ammonia
nitrogen trifluoride
fluoride
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
JP9018755A
Other languages
Japanese (ja)
Inventor
Takashi Jinbo
隆志 神保
Takeshi Yasutake
剛 安武
Isao Harada
功 原田
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.)
Mitsui Chemicals Inc
Original Assignee
Mitsui Chemicals Inc
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 Mitsui Chemicals Inc filed Critical Mitsui Chemicals Inc
Priority to JP9018755A priority Critical patent/JPH10216479A/en
Publication of JPH10216479A publication Critical patent/JPH10216479A/en
Pending legal-status Critical Current

Links

Landscapes

  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)
  • Treating Waste Gases (AREA)

Abstract

PROBLEM TO BE SOLVED: To safely and efficiently treat NF3 by allowing a gas containing the NF3 and ammonia to contact with a catalyst and subjecting at least a part of a product to an adsorptive removal or an absorptive removal by solvent. SOLUTION: After mixing a gas containing the NF3 such as waste gas from a super LSI etching device, waste gas of a CVD clanging gas and leakage gas from a NF3 vessel with the ammonia, the mixture is introduced to a reactor provided with a catalyst such as metal, oxide, carbonate, sulfate and fluoride of Na, K, Cs, Mg, Ca, Sr, Ba, Al and Ga and decomposed. The NF3 is previously diluted with the gas such as nitrogen preferably since a large exothermic reaction is caused when the NF3 is brought into contact with the catalyst. Since hydrogen fluoride is formed as a result of a catalytic reaction with the catalyst, the hydrogen fluoride is adsorbed and removed with a basic oxide such as alkaline earth oxide and soda lime or washed and removed with alkali aq. soln. In such a way, the NF3 is completely and economically removed.

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、三弗化窒素ガス
(以下、NFと称す)の除害方法に関する。
The present invention relates to the nitrogen trifluoride gas about abatement method (hereinafter, referred to as NF 3).

【0002】[0002]

【従来技術】現在、地球環境に悪影響をもたらすフロン
やCOなどに対して規制が行われていることは周知で
あり、NFも自然界ではなかなか分解しない物質であ
る。NFガスは、近年、半導体製造に於いてクリーニ
ングガスとして多量に使用されている。しかし、毒性が
あることから、排ガス中に残存するNFを除去する必
要がある。
2. Description of the Related Art At present, it is well known that restrictions are imposed on chlorofluorocarbons and CO 2 which have a bad influence on the global environment, and NF 3 is also a substance which is not easily decomposed in nature. In recent years, a large amount of NF 3 gas has been used as a cleaning gas in semiconductor manufacturing. However, since it is toxic, it is necessary to remove NF 3 remaining in the exhaust gas.

【0003】上記問題を解決する方法に、高温下で活性
炭を充填したカラムにNFを含む排ガスを通気する方
法(特開昭62−237929号公報)が知られてい
る。しかしながら、この方法では、地球温暖化の原因の
一つとも言われるCFを放出する結果となる。
As a method for solving the above problem, there is known a method in which an exhaust gas containing NF 3 is passed through a column filled with activated carbon at a high temperature (Japanese Patent Application Laid-Open No. 62-237929). However, in this method, resulting in the release of CF 4, also referred to as one of the causes of global warming.

【0004】また、金属酸化物と反応させて除害する方
法(特開平3−181316号公報)も知られている
が、これも約500℃の高温下で反応を行うことに加
え、NOxを生成するという問題がある。
[0004] A method for removing harm by reacting with a metal oxide is also known (Japanese Patent Application Laid-Open No. 3-181316). There is a problem of generating.

【0005】さらに、高温下でガス状のフッ化物を生成
するような金属を充填したカラムにNFを通気する方
法(特開昭61−204025号公報)も知られている
が、これによって生成されるガス状のフッ化物の処理設
備が必要であり、装置が大型化する欠点がある。
Further, a method is known in which NF 3 is passed through a column filled with a metal which generates gaseous fluoride at a high temperature (JP-A-61-204025). It requires a facility for treating gaseous fluorides, which is disadvantageous in that the apparatus becomes large.

【0006】NFを他のガスと反応させて除害する方
法としては水素(特開平2−303524号公報)ある
いは炭化水素(特開平8−131774号公報)と反応
させて分解する方法が公知である。しかし、前者は爆発
範囲の広い水素を使用することに問題があり、後者はC
を放出するので好ましい方法ではない。
As a method for removing NF 3 by reacting with NF 3 with another gas, a method of decomposing by reacting with hydrogen (JP-A-2-303524) or hydrocarbon (JP-A-8-131774) is known. It is. However, the former has a problem in using hydrogen with a wide explosion range, and the latter has C
F 4 not to the preferred method to release.

【0007】[0007]

【発明が解決しようとする課題】本発明は、NFを安
全、かつ効率的に処理する方法を提供することを目的と
したものである。
[0008] The present invention is intended to provide a method of processing a NF 3 safe, and efficient.

【0008】[0008]

【課題を解決するための手段】本発明者らは、従来技術
の欠点を改良し工業的実施の可能な方法について鋭意検
討した結果、NFとアンモニアを用いて触媒と接触す
ることによりNFを除害する方法を見いだし、本発明
を完成したものである。
The present inventors have SUMMARY OF THE INVENTION may, prior disadvantages of the prior improved result of intensive studies on possible ways of industrial implementation, NF 3 by contacting the catalyst with NF 3 and ammonia The present invention has been completed by finding a method for eliminating harmful substances.

【0009】即ち、本発明は三弗化窒素ガスを含むガス
とアンモニアを触媒と接触し、分解すること、そして分
解し、生成物の少なくとも一部を吸着除去すること、さ
らに分解し、生成物の少なくとも一部を溶媒に吸収して
除去することを特徴とする三弗化窒素ガスの除害方法に
関する。
That is, the present invention provides a method for contacting a gas containing nitrogen trifluoride gas and ammonia with a catalyst to decompose and decompose, adsorbing and removing at least a part of the product, further decomposing the product, A method for removing nitrogen trifluoride gas, wherein at least a part of the gas is absorbed by a solvent and removed.

【0010】[0010]

【発明の実施の形態】以下、本発明を更に詳細に説明す
る。本発明の除害方法は超LSIエッチング装置からの
排ガス、CVDクリーニングガスの排ガス、NF容器
からの漏洩ガスなど、NFを含むガスの除害に適用す
る。NFを含むガスはアンモニアと混合された後触媒
を含む反応器に導かれ、分解する。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described below in more detail. The abatement method of the present invention is applied to abatement of a gas containing NF 3 such as an exhaust gas from a super LSI etching apparatus, an exhaust gas of a CVD cleaning gas, and a leak gas from an NF 3 container. After the gas containing NF 3 is mixed with ammonia, it is led to a reactor containing a catalyst and decomposed.

【0011】本発明に用いる触媒は、Na、K、Cs、
Mg、Ca、Sr、Ba、Al、Ga、In、Sn、P
b、Sb、Bi、Cu、Zn、Cd、Sc、Y、La、
Hf、V、Cr、Mn、Tc、Fe、Co、Ni、Z
r、Pd、Os等の金属、酸化物、炭酸塩、硫酸塩、フ
ッ化物等が使用されるが、酸化物等では分解反応で生成
するフッ素化合物によって触媒がフッ素化されるため、
金属フッ化物を用いることが好ましい。
The catalyst used in the present invention is Na, K, Cs,
Mg, Ca, Sr, Ba, Al, Ga, In, Sn, P
b, Sb, Bi, Cu, Zn, Cd, Sc, Y, La,
Hf, V, Cr, Mn, Tc, Fe, Co, Ni, Z
Metals such as r, Pd, and Os, oxides, carbonates, sulfates, fluorides and the like are used. In the case of oxides and the like, the catalyst is fluorinated by a fluorine compound generated by a decomposition reaction.
It is preferable to use metal fluoride.

【0012】触媒の形状は球状、タブレット状、リング
状、破砕品(不定型)等、任意の形状を用いることがで
きる。また、活性成分をアルミナ、チタニア等の担体に
担持することも本願発明の範囲に含まれる。
The catalyst may have any shape such as a sphere, a tablet, a ring, and a crushed product (irregular type). Supporting the active ingredient on a carrier such as alumina or titania is also included in the scope of the present invention.

【0013】触媒と接触する温度は、室温から600℃
の範囲で適宜選択されるが、200〜600℃、好まし
くは300〜550℃が好適である。接触する温度が低
すぎると工業的に許容される速度で反応を進めることが
できず、接触する温度が高すぎると装置の耐熱性、耐食
性に問題が生じ、設備費が高くなるので好ましくない。
The temperature at which the catalyst comes into contact with the catalyst is from room temperature to 600 ° C.
Is suitably selected in the range of 200 to 600 ° C., preferably 300 to 550 ° C. If the contacting temperature is too low, the reaction cannot proceed at an industrially acceptable rate, and if the contacting temperature is too high, the heat resistance and corrosion resistance of the device will be problematic, and equipment costs will increase, which is not preferable.

【0014】添加するアンモニアはNFに対するモル
比で1〜10、好ましくは1〜4が好適である。モル比
が1未満ではNFの分解率が低くなり好ましくない。
また、モル比が10を超えるとNFの分解率は上昇せ
ず、かえって残留アンモニアの処理対策が必要となるの
で好ましくない。
[0014] Ammonia is added in a molar ratio to NF 3 1 to 10, preferably 1 to 4 preferred. When the molar ratio is less than 1, the decomposition rate of NF 3 becomes low, which is not preferable.
On the other hand, when the molar ratio exceeds 10, the decomposition rate of NF 3 does not increase, and it is necessary to take measures for treating residual ammonia, which is not preferable.

【0015】触媒と接触すると大きな発熱反応があるの
で、NFをあらかじめ窒素等のガスで希釈しておくこ
とが好ましい。希釈後のNF濃度は0.1〜10容量
%、好ましくは0.3〜3容量%が好適である。触媒と
接触させる際の空間速度は100〜100,000hr
−1、好ましくは1,000〜50、000hr−1
好ましい。
Since a large exothermic reaction occurs upon contact with the catalyst, NF 3 is preferably diluted in advance with a gas such as nitrogen. The NF3 concentration after dilution is 0.1 to 10% by volume, preferably 0.3 to 3 % by volume. Space velocity at the time of contact with the catalyst is 100 to 100,000 hr
−1 , preferably 1,000 to 50,000 hr −1 .

【0016】NFとアンモニアを触媒と接触させる際
の反応の詳細は明かではないが、反応の結果フッ化水素
が生成する。このフッ化水素はアルカリ土類酸化物やソ
ーダライムのような塩基性酸化物で容易に吸着除去する
ことができる。これらの吸着剤は安価であり、結果とし
てNF除害プロセスのランニングコストが低減され
る。
Although the details of the reaction when NF 3 and ammonia are brought into contact with the catalyst are not clear, hydrogen fluoride is generated as a result of the reaction. This hydrogen fluoride can be easily adsorbed and removed by a basic oxide such as an alkaline earth oxide or soda lime. These adsorbents are inexpensive and result in reduced running costs for the NF 3 abatement process.

【0017】あるいは、フッ化水素をアルカリ性水溶液
で洗浄して除去することもできる。半導体製造プロセス
排ガスの処理ラインにはスクラバーが設置されているこ
とが多く、その場合には既設スクラバーを利用してフッ
化水素を除去するのが有利である。
Alternatively, the hydrogen fluoride can be removed by washing with an alkaline aqueous solution. In many cases, a scrubber is installed in a treatment line for exhaust gas from a semiconductor manufacturing process, and in that case, it is advantageous to remove hydrogen fluoride using an existing scrubber.

【0018】[0018]

【実施例】以下、実施例及び比較例により本発明を更に
詳細に説明する。なお、ガス濃度の%は容量%を表す。 実施例1 フッ化カルシウム(CaF)粉末を打錠成形し、直径
5mm、高さ5mmのタブレットとした。続いてこのタ
ブレットを破砕し、粒径1〜2mmの部分を篩分により
採取した。加熱のためのヒーターを備えた長さ300m
m、内径12mmφのSUS製のカラムに、前記CaF
を5cc充填した。この充填したカラムを350℃に
加熱し、Nガスで希釈されたNF濃度1%のガス5
0cc/minとNガスで希釈されたアンモニア濃度
4%のガス50cc/minをカラム入口の直前で混合
し、カラムに通気した。通気開始から5分後、出口のガ
スをガスクロマトグラフィーで分析した結果、ガス中に
はNFは検出されなかった。また、通気開始から5〜
35分の間、出口ガスを5%水酸化ナトリウム水溶液中
にバブリングさせ、水溶液中のフッ素イオンを定量した
ところ、フィードされたNF中のフッ素分に対応する
量のフッ素イオンが検出された。さらに、通気開始から
24時間後に再度出口のガスをガスクロマトグラフィー
で分析したが、NFは検出されなかった。
The present invention will be described below in more detail with reference to Examples and Comparative Examples. In addition,% of gas concentration represents volume%. Example 1 A tablet having a diameter of 5 mm and a height of 5 mm was formed by tableting calcium fluoride (CaF 2 ) powder. Subsequently, the tablet was crushed, and a portion having a particle size of 1 to 2 mm was collected by sieving. 300m long with heater for heating
m, an inner diameter of 12 mmφ in a SUS column.
2 was filled in 5 cc. The packed column is heated to 350 ° C., and NF 3 gas 1% diluted with N 2 gas 5
0 cc / min and 50 cc / min of a gas having an ammonia concentration of 4% diluted with N 2 gas were mixed immediately before the column inlet, and the mixture was passed through the column. Five minutes after the start of the ventilation, the gas at the outlet was analyzed by gas chromatography. As a result, NF 3 was not detected in the gas. In addition, 5 from the start of ventilation
During 35 minutes, the outlet gas was bubbled into a 5% aqueous sodium hydroxide solution, and the amount of fluorine ions in the aqueous solution was quantified. As a result, an amount of fluorine ions corresponding to the fluorine content in the fed NF 3 was detected. Further, 24 hours after the start of ventilation, the gas at the outlet was again analyzed by gas chromatography, but NF 3 was not detected.

【0019】実施例2〜5 CaFの代わりにフッ化クロム(CrF)、フッ化
コバルト(CoF)、フッ化ストロンチウム(SrF
)、およびフッ化鉄(FeF)を用いた他は実施例
1と同様にしてNFの除害試験を行った。通気開始か
ら5分後および24時間後にカラム出口のガスをガスク
ロマトグラフィーで分析したが、いずれの試験でもNF
は検出されなかった。
[0019] Examples 2-5 chromium fluoride instead of CaF 2 (CrF 2), cobalt fluoride (CoF 2), strontium fluoride (SrF
2 ) and NF 3 removal test was performed in the same manner as in Example 1 except that iron fluoride (FeF 2 ) was used. The gas at the column outlet was analyzed by gas chromatography 5 minutes and 24 hours after the start of aeration.
3 was not detected.

【0020】実施例6 フッ化カルシウム(CaF)粉末を打錠成形し、直径
5mm、高さ5mmのタブレットとした。続いてこのタ
ブレットを破砕し、粒径1〜2mmの部分を篩分により
採取した。加熱のためのヒーターを備えた長さ300m
m、内径12mmφのSUS製のカラムに、前記CaF
を5cc充填した。このカラムの下流に粒径1〜2m
mの酸化カルシウム10ccを充填した長さ150m
m、内径12mmφのSUS製の第2のカラムを接続し
た。CaFを充填したカラムを350℃に加熱し、N
ガスで希釈されたNF濃度1%のガス50cc/m
inとNガスで希釈されたアンモニア濃度4%のガス
50cc/minをカラム入口の直前で混合し、カラム
に通気した。通気開始から5分後、出口のガスをガスク
ロマトグラフィーで分析した結果、ガス中にはNF
検出されなかった。また、通気開始から5〜35分の
間、出口ガスを5%水酸化ナトリウム水溶液中にバブリ
ングさせ、水溶液中のフッ素イオンを定量したが、フッ
素イオンは全く検出されず、NFの分解で生成した含
フッ素ガスは全て酸化カルシウム上に固定されたことが
わかる。さらに、通気開始から24時間後に再度出口の
ガスをガスクロマトグラフィーで分析したが、NF
検出されなかった。
Example 6 A tablet having a diameter of 5 mm and a height of 5 mm was formed by tableting calcium fluoride (CaF 2 ) powder. Subsequently, the tablet was crushed, and a portion having a particle size of 1 to 2 mm was collected by sieving. 300m long with heater for heating
m, an inner diameter of 12 mmφ in a SUS column.
2 was filled in 5 cc. The particle size is 1-2m downstream of this column.
150m long filled with 10cc of calcium oxide
m and a second column made of SUS having an inner diameter of 12 mmφ were connected. The column packed with CaF 2 was heated to 350 ° C.
NF 3 diluted with 2 gas 3 % 1% gas 50cc / m
In and 50 cc / min of a gas having an ammonia concentration of 4% diluted with N 2 gas were mixed immediately before the column inlet and passed through the column. Five minutes after the start of the ventilation, the gas at the outlet was analyzed by gas chromatography. As a result, NF 3 was not detected in the gas. Further, between 5 and 35 minutes from the ventilation started bubbling outlet gas in 5% sodium hydroxide aqueous solution, was quantified fluorine ions in the aqueous solution, the fluorine ion was not detected at all, generated by the decomposition of NF 3 It can be seen that all the fluorine-containing gases thus fixed were fixed on the calcium oxide. Further, 24 hours after the start of ventilation, the gas at the outlet was again analyzed by gas chromatography, but NF 3 was not detected.

【0021】比較例1〜5 アンモニアガスを用いない他は実施例1〜5と同様にし
てNFの除害試験を行った。通気開始から5分後、出
口のガスをガスクロマトグラフィーで分析した結果、N
濃度は0.8〜1%で、減少は認められなかった。
Comparative Examples 1 to 5 NF 3 removal tests were performed in the same manner as in Examples 1 to 5 except that no ammonia gas was used. Five minutes after the start of aeration, the gas at the outlet was analyzed by gas chromatography.
F 3 concentration is 0.8 to 1 percent, a decrease was observed.

【0022】[0022]

【発明の効果】本発明はNFとアンモニアを触媒と接
触させることにより、従来技術では達成されなかったN
を完全に除害することができ、経済的なNF除害
技術を提供することが可能となった。
According to the present invention, by bringing NF 3 and ammonia into contact with a catalyst, N 2 is not achieved by the prior art.
F 3 can harm completely divided, it has become possible to provide an economical NF 3 abatement techniques.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 三弗化窒素ガスを含むガスとアンモニ
アを触媒と接触し、分解することを特徴とする三弗化窒
素ガスの除害方法。
1. A method for removing nitrogen trifluoride gas, comprising decomposing a gas containing nitrogen trifluoride gas and ammonia by contact with a catalyst.
【請求項2】 三弗化窒素ガスを含むガスとアンモニ
アを触媒と接触し、分解し、生成物の少なくとも一部を
吸着除去することを特徴とする三弗化窒素ガスの除害方
法。
2. A method for removing nitrogen trifluoride gas, comprising contacting a gas containing nitrogen trifluoride gas and ammonia with a catalyst to decompose and adsorbing and removing at least a part of a product.
【請求項3】 三弗化窒素ガスを含むガスとアンモニ
アを触媒と接触し、分解し、生成物の少なくとも一部を
溶媒に吸収して除去することを特徴とする三弗化窒素ガ
スの除害方法。
3. A method for removing nitrogen trifluoride gas, comprising: bringing a gas containing nitrogen trifluoride gas and ammonia into contact with a catalyst, decomposing the catalyst, and absorbing and removing at least a part of a product in a solvent. Harm method.
【請求項4】 三弗化窒素ガスに対するアンモニアの
モル比が1〜10である請求項1〜3のいずれか1項に
記載の三弗化窒素ガスの除害方法。
4. The method for removing nitrogen trifluoride gas according to claim 1, wherein the molar ratio of ammonia to nitrogen trifluoride gas is 1 to 10.
【請求項5】 触媒が金属フッ化物である請求項1〜
3のいずれか1項に記載の三弗化窒素ガスの除害方法。
5. The catalyst according to claim 1, wherein the catalyst is a metal fluoride.
3. The method for removing nitrogen trifluoride gas according to any one of 3.
JP9018755A 1997-01-31 1997-01-31 Detoxifying method of gaseous nitrogen trifluoride Pending JPH10216479A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9018755A JPH10216479A (en) 1997-01-31 1997-01-31 Detoxifying method of gaseous nitrogen trifluoride

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9018755A JPH10216479A (en) 1997-01-31 1997-01-31 Detoxifying method of gaseous nitrogen trifluoride

Publications (1)

Publication Number Publication Date
JPH10216479A true JPH10216479A (en) 1998-08-18

Family

ID=11980474

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9018755A Pending JPH10216479A (en) 1997-01-31 1997-01-31 Detoxifying method of gaseous nitrogen trifluoride

Country Status (1)

Country Link
JP (1) JPH10216479A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6921519B2 (en) 2001-01-24 2005-07-26 Ineos Fluor Holdings Limited Decomposition of fluorine containing compounds
JP2007196204A (en) * 2006-01-26 2007-08-09 Kocat Inc Apparatus and method for treating exhaust gas generated from semiconductor manufacturing process
KR100777576B1 (en) 2006-12-15 2007-11-28 동부일렉트로닉스 주식회사 Gas scrubber using nf3 cleaning gas in cvd process and operating method
JP2008246485A (en) * 2008-06-10 2008-10-16 Hitachi Ltd Apparatus for treating perfluoro compounds
WO2010095512A1 (en) * 2009-02-23 2010-08-26 セントラル硝子株式会社 Method and apparatus for decomposing nitrogen trifluoride

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6921519B2 (en) 2001-01-24 2005-07-26 Ineos Fluor Holdings Limited Decomposition of fluorine containing compounds
JP2007196204A (en) * 2006-01-26 2007-08-09 Kocat Inc Apparatus and method for treating exhaust gas generated from semiconductor manufacturing process
KR100777576B1 (en) 2006-12-15 2007-11-28 동부일렉트로닉스 주식회사 Gas scrubber using nf3 cleaning gas in cvd process and operating method
JP2008246485A (en) * 2008-06-10 2008-10-16 Hitachi Ltd Apparatus for treating perfluoro compounds
WO2010095512A1 (en) * 2009-02-23 2010-08-26 セントラル硝子株式会社 Method and apparatus for decomposing nitrogen trifluoride

Similar Documents

Publication Publication Date Title
CA2354205A1 (en) Removal of nitogen oxides from gas streams
JP2005528209A (en) Method for reducing NOx in waste gas streams using chlorine dioxide
US5879646A (en) Treatment of NH3 -containing gases
JP5048208B2 (en) Method and apparatus for treating gas containing fluorine-containing compound
JP4080336B2 (en) Decomposition of fluorine-containing compounds
JPH03106419A (en) Treatment process for gas containing fluorocarbon and catalyst for decomposing fluorocarbon
JP2001338910A (en) Abatement agent for halogen type gas, abatement method and its use
JPH10216479A (en) Detoxifying method of gaseous nitrogen trifluoride
KR920007856B1 (en) Method of removing gassy acidic halogen compound
JPH0716583B2 (en) Method for dry treatment of exhaust gas containing chlorine fluoride
JPH11128675A (en) Removal of chlorine or chlorine compound and apparatus therefor
WO2024135452A1 (en) Exhaust gas treatment method and exhaust gas treatment device
WO2005077496A1 (en) Method and apparatus for treating gas containing fluorine-containing compounds
WO2024135453A1 (en) Discharge gas treatment method and discharge gas treatment device
JP3650588B2 (en) Perfluoro compound recycling method
KR100684201B1 (en) Method for the abatement of waste gas comprising fluorine and its adsorption column device
JP2004181299A (en) Method for detoxifying vent gas
JPH1119472A (en) Method and device of removing nitrogen trifluoride
JPS63190621A (en) Method of removing 1,1,1-trichloroethane out of gas containing 1,1,1-trichloroethane
JPH0483515A (en) Method for decomposing fluorocarbon type cooling medium
JP3515766B2 (en) Removal method of carbon disulfide
RU2009116C1 (en) Method for purifying 1,1,1,2-tetrafluoroethane
JP2002324785A (en) Method for recycling perfluorocompound
JPH1190180A (en) Method for detoxifying nitrogen trifluoride
JPH11179143A (en) Method for treating exhaust gas

Legal Events

Date Code Title Description
A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20051220

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20060418

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20060808