JP3188830B2 - Method and apparatus for removing NF3 exhaust gas - Google Patents
Method and apparatus for removing NF3 exhaust gasInfo
- Publication number
- JP3188830B2 JP3188830B2 JP27482195A JP27482195A JP3188830B2 JP 3188830 B2 JP3188830 B2 JP 3188830B2 JP 27482195 A JP27482195 A JP 27482195A JP 27482195 A JP27482195 A JP 27482195A JP 3188830 B2 JP3188830 B2 JP 3188830B2
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- gas
- water
- hydrogen fluoride
- ammonia
- 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.)
- Expired - Fee Related
Links
Landscapes
- Treating Waste Gases (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、半導体などの製造に伴
い発生するNF3排ガスの除害方法及び除害装置に関す
るものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for removing NF 3 exhaust gas generated during the production of semiconductors and the like.
【0002】[0002]
【従来の技術】近年、NF3は、CVD装置のクリーニ
ング用ガスとして用いられているが、その1/3〜1/2程度
は未反応のまま装置から排出される。NF3は、COと
似た毒性を有するガスであるため、環境中への放出に当
たってはNF3を含む排ガスを予め除害する必要があ
る。2. Description of the Related Art In recent years, NF 3 has been used as a cleaning gas for a CVD apparatus, but about 1/3 to 1/2 of it is discharged from the apparatus without being reacted. Since NF 3 is a gas having a toxicity similar to that of CO, it is necessary to remove exhaust gas containing NF 3 in advance when releasing it into the environment.
【0003】NF3を除害する方法としては、(a)NF3
を含有する気体と水蒸気とを混合し、NF3を水と反応
させて分解する方法(特開平3―65218号公報)、(b)NF3
を含む排ガスを加熱酸化分解すると共に、その酸化分解
生成物とNH3とを反応させる方法(特開平4―290524号
公報)などがある。[0003] As a method of removing NF 3 , (a) NF 3
A gas containing water and NF 3 reacted with water to decompose (JP-A-3-65218), (b) NF 3
And a method of reacting the oxidative decomposition product with NH 3 while heating and oxidatively decomposing an exhaust gas containing the same (JP-A-4-290524).
【0004】しかしながら、上記(a)の方法では、有害
なフッ化水素と共にNOXが多量に副生するため、これ
らの2次除害が必要であること、また、酸性ガスによる
腐食性が大きいことから、高価な材質の装置を必要とす
るなどの問題点がある。また、(b)の方法では、酸性ガ
スによる腐食は低減されるが、反応には外部加熱による
高温度(1000℃程度)が必要であり、さらに分解反応部
内は酸化雰囲気であるためそれに起因する腐食が起こる
ことから、(a)の方法と同様に、高価な材質の装置を必
要とするという問題点がある。However, in the above method (a), since the NO X is produced as a by-product in a large amount with harmful hydrogen fluoride, it is necessary these secondary abatement, also large corrosive by acidic gases Therefore, there is a problem that an expensive material device is required. In addition, in the method (b), corrosion due to acidic gas is reduced, but the reaction requires a high temperature (about 1000 ° C.) by external heating, and furthermore, the decomposition reaction section is in an oxidizing atmosphere, which is caused by it. Since the corrosion occurs, there is a problem that an expensive device is required as in the method (a).
【0005】[0005]
【発明が解決しようとする課題】本発明の目的は、上記
した従来の問題点を解決し、安全で、効率よく、かつ低
コストでNF3排ガスを処理し、環境汚染の問題がない
ように無害化するNF3排ガスの除害方法及び除害装置
を提供することにある。SUMMARY OF THE INVENTION An object of the present invention is to solve the above-mentioned conventional problems and to treat NF 3 exhaust gas safely, efficiently and at low cost so that there is no problem of environmental pollution. It is an object of the present invention to provide a method and apparatus for removing NF 3 exhaust gas which is rendered harmless.
【0006】[0006]
【課題を解決するための手段】本発明者らは、NF3を
含む排ガスをアンモニアガスと混合し、水蒸気の存在
下、還元的雰囲気下において加熱、反応させることによ
り、NF3が窒素とフッ化水素に分解され、生成したフ
ッ化水素をアンモニウム塩として中和、除害することに
より、従来よりも低温で、かつNOxの副生もなくNF3
が無害化されることを見出し、本発明を完成した。即
ち、本発明の要旨は、NF3を含有する気体に、水とア
ンモニアガスとを加え、該混合物を還元的雰囲気下で加
熱、反応させ、NF3を窒素とフッ化水素に分解させる
と共に、生成したフッ化水素をアンモニウム塩として中
和、除害することを特徴とするNF3排ガスの除害方
法、および、そのための装置にある。Means for Solving the Problems The inventors of the present invention mixed NF 3 -containing exhaust gas with ammonia gas, and heated and reacted in a reducing atmosphere in the presence of steam, whereby NF 3 was converted to nitrogen and fluorine. By neutralizing and removing the hydrogen fluoride generated as a result of being decomposed into hydrogen fluoride as an ammonium salt, NF 3 is produced at a lower temperature than before and with no by-product of NO x.
Was found to be harmless, and the present invention was completed. That is, the gist of the present invention is to add water and ammonia gas to a gas containing NF 3 and heat and react the mixture under a reducing atmosphere to decompose NF 3 into nitrogen and hydrogen fluoride. A method for removing NF 3 exhaust gas, which neutralizes and removes generated hydrogen fluoride as an ammonium salt, and an apparatus therefor.
【0007】本発明においては、NF3は水と反応し
て、フッ化水素、NOX等に分解されるものと考えられ
る(2NF3+3H20→N0+N02+6HF)。ここで
生成したフッ化水素はアンモニアと反応してフッ化アン
モニウムとなり、NOXもアンモニアと反応して最終的
に窒素と水に分解される。また、NF3はアンモニアと
も直接反応して窒素とフッ化水素に分解されると考えら
れる(NF3+NH3→N2+3HF)。[0007] In the present invention, NF 3 reacts with water, hydrogen fluoride is believed to be degraded in the NO X, etc. (2NF 3 + 3H 2 0 → N0 + N0 2 + 6HF). The hydrogen fluoride generated here reacts with ammonia to form ammonium fluoride, and NO X also reacts with ammonia to be finally decomposed into nitrogen and water. Further, NF 3 is considered both direct reaction with ammonia is decomposed into hydrogen fluoride and nitrogen (NF 3 + NH 3 → N 2 + 3HF).
【0008】[0008]
【実施の形態】以下、本発明の方法および装置について
詳細に説明する。図1は本発明によるNF3排ガスの除
害装置の概要を示した図である。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the method and apparatus of the present invention will be described in detail. FIG. 1 is a diagram showing an outline of an NF 3 exhaust gas abatement apparatus according to the present invention.
【0009】本発明においては、NF3含有排ガスに水
とアンモニアガスとを加え、酸素、空気等が存在しない
還元的雰囲気下で反応を行う。還元的雰囲気下において
加熱、反応させる方法は特にアンモニアガスは可燃性で
あることから、両ガスを混合するとある濃度範囲で爆鳴
気を形成する。従って、爆鳴気形成を避ける目的でNF
3濃度を1vol%以下、好ましくは0.5vol%以下になるよ
うに希釈する方法が好適である。例えば、NF3含有排
ガスを、N2流入管(11)より供給されるN2により上記の
濃度に希釈すればよい。In the present invention, water and ammonia gas are added to the NF 3 -containing exhaust gas, and the reaction is carried out in a reducing atmosphere free of oxygen, air and the like. In the method of heating and reacting in a reducing atmosphere, particularly, ammonia gas is flammable, so that when both gases are mixed, explosive gas is formed in a certain concentration range. Therefore, for the purpose of avoiding detonation, NF
(3) A method of diluting the solution so that the concentration becomes 1 vol% or less, preferably 0.5 vol% or less is suitable. For example, the NF 3 -containing exhaust gas may be diluted to the above concentration with N 2 supplied from the N 2 inflow pipe (11).
【0010】排ガス流入管(1)より導入されたNF3含有
排ガスは、N2流入管(11)からの窒素ガスで希釈され
る。希釈された排ガスを、入口スクラバー(8)に導入
し、上部より水を噴霧してガスと接触させる事により、
水を添加する。この場合の水の添加量は、排ガス中のN
F3量と比例するが、通常NF3の2倍モル以上が好まし
い。The NF 3 -containing exhaust gas introduced from the exhaust gas inflow pipe (1) is diluted with nitrogen gas from the N 2 inflow pipe (11). By introducing the diluted exhaust gas into the inlet scrubber (8), spraying water from above and bringing it into contact with the gas,
Add water. In this case, the amount of water added is determined by the amount of N in the exhaust gas.
Although it is proportional to the amount of F 3 , it is usually preferably at least twice as much as NF 3 .
【0011】ここで所定量の水を添加された排ガスは、
NH3流入管(6)からNH3ガスを添加されて、反応部(2)
に導かれ、ヒーターエレメント(5)で加熱され、NF3は
水と反応してNOXとフッ化水素に還元分解される。ア
ンモニアの使用量は、NF3およびNF3と水との反応生
成物の量に比例するが、通常NF3の4倍モル以上が好
ましい。The exhaust gas to which a predetermined amount of water has been added is
NH 3 from the inflow pipe (6) is added NH 3 gas, the reaction portion (2)
Is led to and heated by the heater element (5), NF 3 is reduced and decomposed into hydrogen fluoride and NO X react with water. The amount of ammonia used is proportional to the amount of reaction products of NF 3 and NF 3 and water, or 4 fold molar usually NF 3 are preferred.
【0012】本発明で用いる反応部(2)としては特に限
定されず、例えば、反応部の内部に、電気的に温度制御
可能なヒーターエレメントを設けたものが好ましい。反
応温度は通常300℃〜700℃、さらに好ましくは、450℃
〜650℃の範囲である。本発明においては、NF3含有排
ガスの熱分解は、特に酸素、空気等を添加しない還元的
雰囲気下で行われるため、従来の加熱酸化分解に比較し
て、100℃以上低温で反応が可能である。The reaction section (2) used in the present invention is not particularly limited. For example, a reaction section having an electrically controllable heater element inside the reaction section is preferable. Reaction temperature is usually 300 ° C to 700 ° C, more preferably 450 ° C.
In the range of ~ 650 ° C. In the present invention, since the thermal decomposition of the NF 3 -containing exhaust gas is performed in a reducing atmosphere to which oxygen, air, and the like are not added, the reaction can be performed at a low temperature of 100 ° C. or more as compared with the conventional thermal oxidative decomposition. is there.
【0013】更に、NOXおよびフッ化水業はアンモニ
アと反応してN2、H20、フッ化アンモニウムに分解、
中和される。加熱、分解処理された排ガスは引き続き、
出口スクラバー(9)に導入され、水洗処理される。この
水洗処理の方法は特に限定されないが、上部より水を噴
霧して処理ガスと接触させる事により行うことができ
る。これにより、フッ化水素とアンモニアから生成する
フッ化アンモニウムを始めとする水溶性成分を吸収、除
去することができる。冷却水により洗浄冷却されフッ化
アンモニウム等を吸収、除去して無害化した後は、排気
管(4)から排出される。Furthermore, NO X and fluorinated Mizugyo reacts with ammonia N 2, H 2 0, decomposed into ammonium fluoride,
Neutralized. The heated and decomposed exhaust gas continues to
It is introduced into the outlet scrubber (9) and washed with water. The method of this water washing treatment is not particularly limited, but it can be carried out by spraying water from above and contacting with a treatment gas. This makes it possible to absorb and remove water-soluble components such as ammonium fluoride generated from hydrogen fluoride and ammonia. After being washed and cooled with cooling water to absorb and remove ammonium fluoride and the like to render them harmless, they are discharged from the exhaust pipe (4).
【0014】冷却水は給水管(7)から水洗水タンク(3)に
供給され、ポンプ(10)で加圧され、入口スクラバー(8)
および出口スクラバー(9)の給水となる。入口スクラバ
ー(8)は、排ガス中の酸性成分の溶解分離と水供給の機
能を果たす。また、出口スクラバー(9)は、フッ化アン
モニウム、過剰のアンモニアの吸収除害およびガス冷却
が主な機能である。入口スクラバー(8)での酸性水洗水
は、水洗水タンク(3)中の水で中和され排水管(13)から
排出される。Cooling water is supplied from a water supply pipe (7) to a washing water tank (3), is pressurized by a pump (10), and is supplied to an inlet scrubber (8).
And the water is supplied to the outlet scrubber (9). The inlet scrubber (8) performs the functions of dissolving and separating acidic components in the exhaust gas and supplying water. The outlet scrubber (9) has a main function of absorbing and removing ammonium fluoride and excess ammonia, and gas cooling. The acidic washing water in the inlet scrubber (8) is neutralized by the water in the washing water tank (3) and discharged from the drain pipe (13).
【0015】[0015]
[実施例1]排ガス流入管(1)より10vol%のNF3を含む
窒素を5リットル/分で、N2流入管(11)より窒素を250リ
ットル/分でそれぞれ入口スクラバー(8)に導入し、水を
水蒸気換算で5リットル/分になるように添加した。次
に、NH3流入管(6)からNH3ガスを、10リットル/分で
添加し、反応部(2)に導入し、反応温度550℃、接触時間
5秒で反応させた。反応後のガスは出口スクラバー(9)
で水洗した。出口ガス中のNF3ガス濃度は5ppm、NO
X濃度は3ppm以下、フッ化水素濃度は0.5ppm以下で
あった。[Example 1] Nitrogen containing 10 vol% of NF 3 was introduced into the inlet scrubber (8) from the exhaust gas inlet pipe (1) at 5 liter / minute and nitrogen from the N 2 inlet pipe (11) at 250 liter / minute. Then, water was added at a rate of 5 liters / minute in terms of steam. Then, NH 3 gas from the NH 3 inlet tube (6), was added at 10 l / min was introduced into the reaction unit (2), reaction temperature 550 ° C., and reacted at the contact time of 5 seconds. The gas after the reaction is the outlet scrubber (9)
And washed with water. NF 3 gas concentration in outlet gas is 5ppm, NO
The X concentration was 3 ppm or less, and the hydrogen fluoride concentration was 0.5 ppm or less.
【0016】[実施例2]NF3を約1.5vol%含むCV
Dクリーニング排ガスを50リツトル/分で排ガス流入管
(1)より導入する以外は、実施例1と同じ条件で処理し
た。出口ガス中のNF3ガス濃度は8ppm、NOX濃度は
5ppm以下、フッ化水素濃度は0.5ppm以下であった。Example 2 CV containing about 1.5 vol% of NF 3
D cleaning exhaust gas at 50 l / min
Except for introducing from (1), treatment was performed under the same conditions as in Example 1. NF 3 gas concentration in the outlet gas is 8 ppm, NO X concentration 5ppm or less, the hydrogen fluoride concentration was less than 0.5 ppm.
【0017】[0017]
【発明の効果】本発明により、比較的低温で、しかも短
時間でNF3の分解が可能となり、NOXの副生や装置の
腐食も無く、安全で、ランニングコストが低廉なNF3
排ガスの除害方法および除害装置を提供することができ
る。According to the present invention, NF 3 can be decomposed at a relatively low temperature and in a short time, and there is no by-product of NO X or corrosion of the device, and NF 3 is safe and has a low running cost.
An exhaust gas removing method and a removing device can be provided.
【図1】本発明によるNF3排ガスの除害装置の概要を
示した図。FIG. 1 is a diagram showing an outline of an NF 3 exhaust gas abatement apparatus according to the present invention.
(1) 排ガス流入管 (2) 反応部 (3) 水洗水タンク (4) 排気管 (5) ヒーターエレメント (6) NH3流入管 (7) 給水管 (8) 入口スクラバー (9) 出口スクラバー (10) ポンプ (11) N2流入管 (12) 邪魔板 (13) 排水管(1) Exhaust gas inlet pipe (2) Reactor (3) Rinse water tank (4) Exhaust pipe (5) Heater element (6) NH 3 inlet pipe (7) Feed pipe (8) Inlet scrubber (9) Outlet scrubber ( 10) Pump (11) N 2 inlet pipe (12) Baffle plate (13) Drain pipe
───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平3−65218(JP,A) 特開 平4−290524(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01D 53/68 B01D 53/54 ────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-3-65218 (JP, A) JP-A-4-290524 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B01D 53/68 B01D 53/54
Claims (2)
アガスとを加え、該混合物を還元的雰囲気下で加熱、反
応させ、NF3を窒素とフッ化水素に分解させると共
に、生成したフッ化水素をアンモニウム塩として中和、
除害することを特徴とするNF3排ガスの除害方法。1. Water and ammonia gas are added to a gas containing NF 3 , and the mixture is heated and reacted under a reducing atmosphere to decompose NF 3 into nitrogen and hydrogen fluoride, and to generate HF. Neutralizes hydrogen hydride as ammonium salt,
A method for removing NF 3 exhaust gas, which comprises removing the harmful substances.
アガスとを加え、該混合物を還元的雰囲気下で加熱、反
応させ、NF3を窒素とフッ化水素に分解させる反応部
を有する加熱分解装置と、生成したフッ化水素をアンモ
ニウム塩として中和、除害する除害装置とから構成され
ることを特徴とするNF3排ガスの除害装置。2. A heating unit having a reaction unit for adding water and ammonia gas to a gas containing NF 3 and heating and reacting the mixture in a reducing atmosphere to decompose NF 3 into nitrogen and hydrogen fluoride. An abatement device for NF 3 exhaust gas, comprising: a decomposition device; and an abatement device that neutralizes and removes generated hydrogen fluoride as an ammonium salt.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP27482195A JP3188830B2 (en) | 1995-09-27 | 1995-09-27 | Method and apparatus for removing NF3 exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP27482195A JP3188830B2 (en) | 1995-09-27 | 1995-09-27 | Method and apparatus for removing NF3 exhaust gas |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0985045A JPH0985045A (en) | 1997-03-31 |
JP3188830B2 true JP3188830B2 (en) | 2001-07-16 |
Family
ID=17547045
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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JP27482195A Expired - Fee Related JP3188830B2 (en) | 1995-09-27 | 1995-09-27 | Method and apparatus for removing NF3 exhaust gas |
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Country | Link |
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JP (1) | JP3188830B2 (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB9919002D0 (en) * | 1999-08-12 | 1999-10-13 | Boc Group Plc | Removal of noxious substances from gas streams |
JP4828722B2 (en) * | 2001-05-21 | 2011-11-30 | ルネサスエレクトロニクス株式会社 | Abatement equipment |
KR100428905B1 (en) * | 2001-09-07 | 2004-04-28 | 주식회사 소디프신소재 | A process for preparing highly pure potassium fluoride from nitrogen trifluoride composite gas |
JP5986852B2 (en) * | 2012-09-03 | 2016-09-06 | 株式会社ジャパンディスプレイ | Electrothermal gas abatement system |
-
1995
- 1995-09-27 JP JP27482195A patent/JP3188830B2/en not_active Expired - Fee Related
Also Published As
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JPH0985045A (en) | 1997-03-31 |
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