JPH0515740A - Treatment of nitrogen trifluoride-containing exhaust gas - Google Patents

Treatment of nitrogen trifluoride-containing exhaust gas

Info

Publication number
JPH0515740A
JPH0515740A JP3172243A JP17224391A JPH0515740A JP H0515740 A JPH0515740 A JP H0515740A JP 3172243 A JP3172243 A JP 3172243A JP 17224391 A JP17224391 A JP 17224391A JP H0515740 A JPH0515740 A JP H0515740A
Authority
JP
Japan
Prior art keywords
exhaust gas
activated carbon
gas
nitrogen trifluoride
containing exhaust
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
JP3172243A
Other languages
Japanese (ja)
Other versions
JP3269565B2 (en
Inventor
Itsuo Orihara
逸雄 折原
Moriyuki Fukushima
守之 福島
Shiro Sato
四郎 佐藤
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.)
Kanto Denka Kogyo Co Ltd
Original Assignee
Kanto Denka Kogyo 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 Kanto Denka Kogyo Co Ltd filed Critical Kanto Denka Kogyo Co Ltd
Priority to JP17224391A priority Critical patent/JP3269565B2/en
Publication of JPH0515740A publication Critical patent/JPH0515740A/en
Application granted granted Critical
Publication of JP3269565B2 publication Critical patent/JP3269565B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime 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
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/30Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]

Landscapes

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

Abstract

PURPOSE:To improve the defect of a nitrogen trifluoride (NF3)containing exhaust gas treatment method provided heretofore and to simply and efficiently treat NF3-containing exhaust gas to reduce the concn. of NH3 to a level not generating a problem from the aspect of air pollution or working environment. CONSTITUTION:Exhaust gas containing nitrogen trifluoride (NF3) is brought into contact with a mixture consisting of activated carbon and metal oxide at 200-600 deg.C to be reacted therewith to be made harmless.

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、ドライエッチング等に
使用した三弗化窒素(NF3)含有排ガスを分解除去す
る方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for decomposing and removing exhaust gas containing nitrogen trifluoride (NF 3 ) used for dry etching or the like.

【0002】NF3は、従来高エネルギー燃料の酸化剤
として、又化学レーザーの弗素源として賞用されてきた
が、近年処理後残渣の残らない超LSI用ドライエッチ
ングガスとして又CVD(化学気相成長法)装置用のク
リーニングガスとして注目を集めている有用なガスであ
る。
NF 3 has hitherto been prized as an oxidizer for high-energy fuels and as a fluorine source for chemical lasers, but in recent years, it has also been used as a dry etching gas for ultra-LSI, which leaves no residue after processing, and CVD (chemical vapor phase). It is a useful gas that has been attracting attention as a cleaning gas for growth equipment.

【0003】一方NF3は、常温では非常に安定で水や
酸、アルカリ水溶液とも反応しない不燃性のガスである
が、許容濃度10ppmの毒性ガスである。
On the other hand, NF 3 is a non-flammable gas that is very stable at room temperature and does not react with water, acid or alkaline aqueous solution, but is a toxic gas with an allowable concentration of 10 ppm.

【0004】このため使用後のNF3含有排ガスをその
まま大気中に放出する事はできず、空気で10ppm以
下に希釈して排出するか、あるいは何らかの分解処理を
した上で排出しているのが現状である。
For this reason, the NF 3 -containing exhaust gas after use cannot be released into the atmosphere as it is, and it is diluted with air to 10 ppm or less and then discharged, or it is discharged after some decomposition treatment. The current situation.

【0005】しかしながら、空気希釈の上排出されるN
3は大気中では分解されないため、今後のNF3の使用
量増加見込とあいまって自然環境特に生物体系への悪影
響が懸念されている。
However, the N discharged after dilution with air
Since F 3 is not decomposed in the atmosphere, it is feared that the use of NF 3 will increase in the future and that the natural environment, especially the biological system, will be adversely affected.

【0006】[0006]

【従来の技術】従来NF3またはNF3含有ガスを分解処
理する方法として次の方法が知られている。
2. Description of the Related Art Conventionally, the following method has been known as a method for decomposing NF 3 or NF 3 -containing gas.

【0007】(1)加熱した金属と反応させる方法 この方法では、生成した金属フッ化物が固体の場合に
は、金属フッ化物が金属表面に皮膜を形成するために反
応が阻害され短時間のうちにNF3分解能力が低下す
る。
(1) Method of reacting with heated metal In this method, when the produced metal fluoride is a solid, the reaction is inhibited because the metal fluoride forms a film on the metal surface, and the reaction is continued within a short time. In addition, the ability to decompose NF 3 decreases.

【0008】又金属フッ化物が粉体のために反応器或い
は配管の閉塞を起し易い。
Further, since the metal fluoride is a powder, it tends to cause clogging of the reactor or piping.

【0009】生成フッ化物がガス状である場合、二次処
理としてこれを物理吸着或いはアルカリ洗浄せねばなら
ず装置が大型化し、又装置の腐食も著しいという欠点を
有する。
When the produced fluoride is in a gaseous state, it has to be physically adsorbed or washed with an alkali as a secondary treatment, so that the apparatus becomes large in size and the apparatus is corroded remarkably.

【0010】(2)高温の活性炭と反応させる方法 この方法では400℃以上の反応温度で比較的効果率良
くNF3を分解できるが、同時にNF3よりも毒性が強く
かつ爆発性を有する二弗化二窒素(N22)が大量に副
生する。N22の副生を抑えるためにはNF3と活性炭
との接触時間を極めて長くしかつ反応温度を500℃以
上の高温にせねばならない。この場合生成するCF4
26等のフロロカーボンとNF3とがN22の爆発に
より誘爆を起す危険がある。又処理対象ガス中にO2
混在すると活性炭の燃焼が起きる事があり、いずれにし
ても工業的に有効な方法とは言い難い。
(2) Method of reacting with high temperature activated carbon This method can decompose NF 3 at a reaction temperature of 400 ° C. or higher with relatively high efficiency, but at the same time, it is more toxic and explosive than NF 3. Nitrous oxide (N 2 F 2 ) is produced as a large amount as a by-product. In order to suppress the production of N 2 F 2 as a by-product, the contact time between NF 3 and activated carbon must be extremely long and the reaction temperature must be 500 ° C. or higher. CF 4 generated in this case,
There is a risk that fluorocarbons such as C 2 F 6 and NF 3 may cause an explosion due to the explosion of N 2 F 2 . Further, if O 2 is mixed in the gas to be treated, combustion of activated carbon may occur, and in any case, it cannot be said to be an industrially effective method.

【0011】[0011]

【発明が解決しようとする課題】上記のようにNF3
有排ガスの分解処理法については、いくつかの方法が提
案されているが、装置上及び反応面で問題点が多く、又
効率面で決め手となる方法が確立されていないのが現状
である。
As described above, several methods have been proposed for the decomposition treatment method of NF 3 -containing exhaust gas, but there are many problems in terms of equipment and reaction, and in terms of efficiency. At present, the decisive method has not been established.

【0012】そこで、本発明は従来提案されて来たこれ
らNF3含有排ガス処理法の欠点を改良し簡便かつ効率
的にNF3含有排ガスを処理し、大気汚染又は作業環境
上問題のない濃度迄無害化する方法を提供するものであ
る。
Therefore, the present invention improves the drawbacks of these NF 3 -containing exhaust gas treatment methods that have hitherto been proposed, and simply and efficiently treats NF 3 -containing exhaust gas to a concentration at which there is no problem in air pollution or working environment. It provides a way to render it harmless.

【0013】[0013]

【課題を解決するための手段】本発明は、前記した従来
法の問題点を一挙に解決した工業的に極めて有効なNF
3の除害方法を提供するものであり、具体的には、NF3
を含む排ガスを活性炭とMgO,BaO,Al23,T
iO2,ZnO,CaO等の金属酸化物の少なくとも1
種との混合物と200〜600℃の温度範囲で接触反応
させ無害化するものである。
The present invention is an industrially extremely effective NF which solves the above-mentioned problems of the conventional method all at once.
3 provides a method of removing harm. Specifically, NF 3
Exhaust gas containing activated carbon, MgO, BaO, Al 2 O 3 , T
At least one of metal oxides such as iO 2 , ZnO and CaO
It is made harmless by reacting with a mixture with a seed in a temperature range of 200 to 600 ° C.

【0014】本発明による処理後のガス組成はN2,C
4,CO2から成り、毒性及び爆発性を有するN22
全く副生しないため、生成ガスの二次処理の必要が無
く、そのまま大気中に排出する事ができる。
The gas composition after treatment according to the invention is N 2 , C
Since N 2 F 2 which is composed of F 4 and CO 2 and has toxicity and explosiveness is not by-produced at all, it is possible to directly discharge the produced gas into the atmosphere without the need for secondary treatment.

【0015】本発明で処理できるNF3ガス濃度は10
0%は勿論のこと、He,Ar,N2や空気で希釈した
ガスについても適用できる。
The concentration of NF 3 gas which can be treated by the present invention is 10
Not only 0%, but also He, Ar, N 2 and a gas diluted with air can be applied.

【0016】又、反応温度は、活性炭と併用する金属酸
化物の種類により異なるが一般に200〜600℃、よ
り好ましくは300〜500℃の温度が選択される。2
00℃以下ではNF3り分解が不十分であり、又600
℃以上では反応器材質の劣化が起き易い。
The reaction temperature is generally 200 to 600 ° C., more preferably 300 to 500 ° C., though it depends on the kind of metal oxide used in combination with the activated carbon. Two
If the temperature is less than 00 ° C, the decomposition of NF 3 is insufficient.
Deterioration of the reactor material is likely to occur at temperatures above ℃.

【0017】反応時間は、用いる金属酸化物の種類や活
性炭との混合比率、処理すべきガス中のNF3濃度によ
り異なるが1秒〜10分間の間で適宜選択される。1秒
以下ではNF3の分解が不十分であり、又10分間以上
ではNOxが副生するため好ましくない。
The reaction time varies depending on the type of metal oxide used, the mixing ratio with activated carbon, and the NF 3 concentration in the gas to be treated, but is appropriately selected from 1 second to 10 minutes. If it is less than 1 second, the decomposition of NF 3 is insufficient, and if it is more than 10 minutes, NOx is by-produced, which is not preferable.

【0018】活性炭は、成型炭でも破砕炭でも使用可能
であるが触媒層での圧力損失とガスとの接触面積双方を
考慮して4〜8メッシュの粒状もしくは破砕片である事
が望ましい。
Although the activated carbon may be used in the form of crushed coal or crushed coal, it is desirable that the activated carbon be granular or crushed pieces of 4 to 8 mesh in consideration of both the pressure loss in the catalyst layer and the contact area with gas.

【0019】活性炭と併用する金属酸化物は粉体のまま
使用しても良いが、反応器内の圧力損失あるいは閉塞を
防ぐため予め4〜8メッシュの粒状に成型して使用する
事が望ましい。
The metal oxide used in combination with the activated carbon may be used as it is as a powder, but it is desirable to use it by molding it into a granular form of 4 to 8 mesh in advance in order to prevent pressure loss or blockage in the reactor.

【0020】活性炭と金属酸化物との混合方法は、各々
を所定の比率で混合して使用しても良いし、各々を微粉
砕し、これにタールピッチ等を加えて良く混和した後、
造粒機にかけて所定の粒度に成型後加熱焼成した一体型
触媒として使用しても良い。
The activated carbon and the metal oxide may be mixed at a predetermined ratio and used, or each may be finely pulverized and tar pitch or the like may be added thereto and well mixed,
It may be used as an integrated catalyst which is obtained by molding with a granulator into a predetermined particle size, followed by heating and firing.

【0021】活性炭と金属酸化物との混合割合は、各々
10〜90wt%の範囲で任意に選択すれば良いが、触
媒ライフと効果を考慮して活性炭50〜90wt%金属
酸化物10〜50wt%の範囲で選択する事が望まし
い。
The mixing ratio of the activated carbon and the metal oxide may be arbitrarily selected within the range of 10 to 90 wt%, but in consideration of the catalyst life and effect, the activated carbon is 50 to 90 wt% and the metal oxide is 10 to 50 wt%. It is desirable to select within the range.

【0022】反応器は、気体と固体とを触媒できるもの
であれば特に型状の制限はないが、固定床流通式、流動
層式強制循環式などの接触効率が良好なものであれば更
に好適である。
The reactor is not particularly limited in its shape as long as it can catalyze gas and solid. However, if the contact efficiency is a fixed bed flow type, a fluidized bed type forced circulation type or the like, it is further preferable. It is suitable.

【0023】又、その材質は、ニッケル、モネル等の耐
フッ素材料の使用が好ましい。
As the material, it is preferable to use a fluorine-resistant material such as nickel or monel.

【0024】[0024]

【実施例】本発明の方法を以下実施例によりさらに説明
するが、本発明はこれらの実施例に限定されるものでは
ない。
The method of the present invention will be further described with reference to the following examples, but the present invention is not limited to these examples.

【0025】[0025]

【実施例1】内径40mm長さ1000mmのニッケル
製反応管に6〜8メッシュの粒状活性炭160gと4〜
6メッシュに成型した粒状酸化マグネシウム80gを良
く混合して充填し外部ヒーターにより反応管を400℃
に保持した後100%NF3を0.5l/分で供給し
た。2時間経過後の排出ガス組成をガスクロマトグラフ
ィーで分析した結果、NF3が3ppmで他はN2とCO
2とCF4であった。
Example 1 In a nickel reaction tube having an inner diameter of 40 mm and a length of 1,000 mm, 160 g of 6-8 mesh granular activated carbon and 4-
80 g of granular magnesium oxide molded into 6 mesh was mixed well and filled, and the reaction tube was heated to 400 ° C by an external heater.
Then, 100% NF 3 was supplied at 0.5 l / min. As a result of analyzing the composition of the exhaust gas after 2 hours by gas chromatography, NF 3 was 3 ppm, and the others were N 2 and CO.
2 and CF 4 .

【0026】[0026]

【実施例2】供給ガスをNF3:10vol%及びH
e:90vol%の組成とした以外は実施例1と同様の
反応を行なった。排出ガス組成はHe以外にN2とCO2
のみでCF3は検出されなかった。
Example 2 NF 3 : 10 vol% and H as feed gas
e: The same reaction as in Example 1 was performed except that the composition was 90 vol%. Exhaust gas composition is N 2 and CO 2 in addition to He
CF 3 was not detected by itself.

【0027】[0027]

【実施例3】実施例1と同様の反応器に6〜8メッシュ
粒状活性炭160gと4〜6メッシュの粒状酸化亜鉛8
0gの混合物を充填し、反応管を300℃に保持した後
NF3:10vol%及びHe:90vol%の混合ガ
スを1l/分で供給した。2時間後の排出ガス組成はH
e以外にN2とCO2のみでNF3は検出されなかった。
Example 3 In a reactor similar to that of Example 1, 160 g of 6-8 mesh granular activated carbon and 4-6 mesh granular zinc oxide 8 were used.
After charging 0 g of the mixture and keeping the reaction tube at 300 ° C., a mixed gas of NF 3 : 10 vol% and He: 90 vol% was supplied at 1 l / min. Exhaust gas composition after 2 hours is H
Other than e, NF 3 was not detected with only N 2 and CO 2 .

【0028】[0028]

【実施例4】実施例1と同様の反応器に6〜8メッシュ
粒状活性炭200gと4〜6メッシュの粒状酸化アルミ
ニウム50gの混合物を充填し、反応管を300℃に保
持後NF3:5vol%,O2:5vol%及びHe:9
0vol%の混合ガスを1l/分で供給した。2時間後
の排出ガス組成はHe以外にN2とCO2のみでNF3
検出されなかった。又、供給ガスへのO2の添加によ
る、活性炭の燃焼等異常反応は認められなかった。
Example 4 A reactor similar to that of Example 1 was filled with a mixture of 200 g of 6-8 mesh granular activated carbon and 50 g of 4-6 mesh granular aluminum oxide, and the reaction tube was kept at 300 ° C. and NF 3 : 5 vol%. , O 2 : 5 vol% and He: 9
A 0 vol% mixed gas was supplied at 1 l / min. The composition of the exhaust gas after 2 hours was N 2 and CO 2 other than He, and NF 3 was not detected. No abnormal reaction such as combustion of activated carbon due to addition of O 2 to the supply gas was observed.

【0029】[0029]

【実施例5】実施例1と同様の反応器に活性炭粉末と酸
化鉄粉末を重量で3:1の割合で混合し、4〜6メッシ
ュの粒度に成型した触媒300gを充填し、反応管を3
00℃に保持後NF3:10vol%及びHe:90v
ol%の混合ガスを1l/分で供給した。
Example 5 A reactor similar to that in Example 1 was mixed with activated carbon powder and iron oxide powder in a weight ratio of 3: 1 and charged with 300 g of a catalyst molded to a particle size of 4 to 6 mesh. Three
After holding at 00 ° C, NF 3 : 10 vol% and He: 90v
An ol% mixed gas was supplied at 1 l / min.

【0030】2時間後の排出ガス組成はHe以外にN2
とCO2のみでNF3は検出されなかった。
After 2 hours, the composition of the exhaust gas was N 2 in addition to He.
And CO 2 alone, no NF 3 was detected.

【0031】[0031]

【比較例】実施例1と同様の反応器に6〜8メッシュ粒
状活性炭200gを充填し、反応管を300℃に保持
後、NF3:10vol%及びHe:90vol%の混
合ガスを1l/分で供給した。
Comparative Example A reactor similar to that of Example 1 was charged with 200 g of 6-8 mesh granular activated carbon, the reaction tube was kept at 300 ° C., and then a mixed gas of NF 3 : 10 vol% and He: 90 vol% was added at 1 l / min. Supplied by.

【0032】2時間後の排出ガス組成はHe以外にNF
3:25ppm,N22:11.8vol%その他はN2
であった。
Exhaust gas composition after 2 hours was NF in addition to He
3 : 25 ppm, N 2 F 2 : 11.8 vol% and others N 2
Met.

【0033】[0033]

【発明の効果】本発明によれば、NF3含有排ガス流
を、活性炭/金属酸化物混合物床を含む比較的簡易な装
置中で昇温において接触処理することにより、そのNF
3分を安全な生成物に効率的に分解し、かくして大気中
へそのまま放出できる無害化された排ガス流が得られ
る。従って本発明は、NF3ガスを工業的により安全に
使用する道を拓くと共に環境保護に寄与するところ大で
ある。
According to the present invention, the NF 3 -containing exhaust gas stream is catalytically treated at elevated temperature in a relatively simple apparatus containing a bed of activated carbon / metal oxide mixture to produce NF 3
Efficiently breaks down 3 minutes into a safe product, thus obtaining a detoxified exhaust gas stream that can be released directly into the atmosphere. Therefore, the present invention greatly opens up a way to use NF 3 gas industrially and safely and contributes to environmental protection.

Claims (1)

【特許請求の範囲】 【請求項1】 三弗化窒素を含有する排ガスを、活性炭
と金属酸化物とからなる混合物と200〜600℃の範
囲の温度で反応させることを特徴とする三弗化窒素含有
排ガスの処理方法。
Claim: What is claimed is: 1. An exhaust gas containing nitrogen trifluoride is reacted with a mixture of activated carbon and a metal oxide at a temperature in the range of 200 to 600 ° C. Method for treating nitrogen-containing exhaust gas.
JP17224391A 1991-07-12 1991-07-12 Treatment method for exhaust gas containing nitrogen trifluoride Expired - Lifetime JP3269565B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17224391A JP3269565B2 (en) 1991-07-12 1991-07-12 Treatment method for exhaust gas containing nitrogen trifluoride

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17224391A JP3269565B2 (en) 1991-07-12 1991-07-12 Treatment method for exhaust gas containing nitrogen trifluoride

Publications (2)

Publication Number Publication Date
JPH0515740A true JPH0515740A (en) 1993-01-26
JP3269565B2 JP3269565B2 (en) 2002-03-25

Family

ID=15938274

Family Applications (1)

Application Number Title Priority Date Filing Date
JP17224391A Expired - Lifetime JP3269565B2 (en) 1991-07-12 1991-07-12 Treatment method for exhaust gas containing nitrogen trifluoride

Country Status (1)

Country Link
JP (1) JP3269565B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0895801A2 (en) * 1997-08-07 1999-02-10 Showa Denko Kabushiki Kaisha Method for decomposing nitrogen fluoride or sulfur fluoride and decomposing reagent used therefor
CN104399369A (en) * 2014-12-17 2015-03-11 山东应天节能环保科技有限公司 Gas phase combined desulfurization and denitration method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0895801A2 (en) * 1997-08-07 1999-02-10 Showa Denko Kabushiki Kaisha Method for decomposing nitrogen fluoride or sulfur fluoride and decomposing reagent used therefor
EP0895801A3 (en) * 1997-08-07 1999-04-14 Showa Denko Kabushiki Kaisha Method for decomposing nitrogen fluoride or sulfur fluoride and decomposing reagent used therefor
CN104399369A (en) * 2014-12-17 2015-03-11 山东应天节能环保科技有限公司 Gas phase combined desulfurization and denitration method

Also Published As

Publication number Publication date
JP3269565B2 (en) 2002-03-25

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