JPH0679138A - Method for pretreating nf3 gas - Google Patents
Method for pretreating nf3 gasInfo
- Publication number
- JPH0679138A JPH0679138A JP4234516A JP23451692A JPH0679138A JP H0679138 A JPH0679138 A JP H0679138A JP 4234516 A JP4234516 A JP 4234516A JP 23451692 A JP23451692 A JP 23451692A JP H0679138 A JPH0679138 A JP H0679138A
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- JP
- Japan
- Prior art keywords
- gas
- hydrogen bromide
- hydroxide
- removal
- outlet
- 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.)
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Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、NF3 ガスと臭化水素
等を同時に扱うシステムにおいてNF3 ガスを安全に除
害するための前処理方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a pretreatment method for safely removing NF 3 gas in a system that simultaneously handles NF 3 gas and hydrogen bromide.
【0002】[0002]
【従来の技術および解決すべき問題点】NF3 は航空宇
宙分野ではロケットの燃料として、また近年半導体産業
分野ではCVD装置等のドライクリーニング剤あるいは
LSI製造工程でのドライエッチング剤として注目され
ている。特にドライエッチング剤としてはCF4 などの
パーフロロカーボン系のエッチング剤に比較してLSI
に対する汚染の度合がきわめて少ないという利点があり
次第に多用されるようになってきている。2. Description of the Related Art NF 3 attracts attention as a rocket fuel in the aerospace field, and in recent years as a dry cleaning agent for a CVD apparatus or a dry etching agent in an LSI manufacturing process in the semiconductor industry field. . Especially as a dry etching agent, LSI is more suitable than perfluorocarbon type etching agents such as CF 4.
It has been increasingly used because it has the advantage of being extremely low in pollution.
【0003】しかしながらNF3 は大気中できわめて安
定であり、水にもわずかしか溶解しないTLV=10p
pmの毒性ガスであるため、これを使用する場合にはそ
の未利用ガスを排出するときにその除害が常に必要とな
ってくる。However, NF 3 is extremely stable in the atmosphere and is only slightly soluble in water. TLV = 10 p
Since this is a pm toxic gas, it is always necessary to remove the unused gas when it is used.
【0004】一方CVD装置では同時に用いられること
の多い臭化水素、塩化水素、臭素、塩素のうち少なくと
も一種以上の成分(以下「臭化水素等」という)ととも
に安全に除害する方法が求められている。On the other hand, in a CVD apparatus, a method for safely removing harm together with at least one component (hereinafter referred to as "hydrogen bromide, etc.") of hydrogen bromide, hydrogen chloride, bromine and chlorine which are often used at the same time is required. ing.
【0005】NF3 は常温付近では非常に安定なガス
で、酸・アルカリ等の化学物質とは全く反応せず、水に
ほとんど吸収されずまた適当な吸着剤もないため通常の
化学的・物理的な方法では除害できない。しかしNF3
は180℃以上でN2 と活性なF原子に分解し始め(式
1)、400℃以上で十分大きな分解速度を持つように
なる。NF 3 is a very stable gas near room temperature, does not react with chemical substances such as acids and alkalis, is hardly absorbed by water, and has no suitable adsorbent. Can not be removed by a traditional method. But NF 3
Starts to decompose into N 2 and active F atoms at 180 ° C or higher (Equation 1), and has a sufficiently large decomposition rate at 400 ° C or higher.
【0006】 2NF3 → N2 + 6F (式1) つまり、NF3 を処理するための有効な方法は400℃
以上の高温でNF3 を分解し、発生したF原子を適当な
物質と反応させるというもので、これまで工業的用途に
開発されたNF3 の除害方法の大部分のものはこの原理
に基づいている。例えばFと反応する物質としてSi、
W、Mo等の揮発性フッ化物を生成するものを利用する
方法(特公昭63-48570号)、活性炭などCF4 ガスを生
成する炭素源を利用する方法(特公平2-30731 号)など
である。2NF 3 → N 2 + 6F (Equation 1) That is, an effective method for treating NF 3 is 400 ° C.
NF 3 is decomposed at the above high temperature and the generated F atoms are reacted with an appropriate substance. Most of the NF 3 detoxification methods that have been developed for industrial use are based on this principle. ing. For example, as a substance that reacts with F, Si,
Methods that use volatile fluorides such as W and Mo (Japanese Patent Publication No. 63-48570) and carbon sources that generate CF 4 gas such as activated carbon (Japanese Patent Publication No. 2-30731) is there.
【0007】ところでNF3 の主要用途である半導体製
造等におけるクリーニングおよびエッチング工程ではN
F3 に臭化水素等を混合して用いることが多いが、臭化
水素等のガスはNF3 を分解除害する高温の反応器にお
いてはその金属材質を著しく腐食させてしまう。こうし
た危険を除くための、臭化水素等をNF3 の除害反応の
前段で予め除去する方法としてはこれまで適当なものが
提案されていなかった。By the way, in the cleaning and etching processes in semiconductor manufacturing, which is the main use of NF 3 ,
F 3 is often used a mixture of hydrogen bromide in, but gases such as hydrogen bromide would significantly corrode the metal material in the high temperature reactor harm min releasing NF 3. As a method for removing hydrogen bromide and the like in advance before the NF 3 removal reaction to remove such a danger, no suitable method has been proposed so far.
【0008】[0008]
【問題点を解決するための手段】本発明は、上記の実状
に鑑みてなされたもので、高温部を有するNF3 の除害
装置の前段に臭化水素等を除去する薬剤を配して安全に
NF3 の除害を行うことができるという方法を提供する
ものであり、さらには臭化水素等を除去する薬剤の寿命
を管理し得る方法をも提供するものである。SUMMARY OF THE INVENTION The present invention has been made in view of the above situation, in which a chemical agent for removing hydrogen bromide or the like is arranged in front of an NF 3 abatement device having a high temperature part. It is intended to provide a method capable of safely removing NF 3 , and further to provide a method capable of controlling the life of a chemical agent for removing hydrogen bromide and the like.
【0009】すなわち本発明は、NF3 ガスを除害する
工程に先立ち、NF3 ガスと共存している臭化水素、塩
化水素、臭素、塩素を除去薬剤を用いて反応除去するこ
とを特徴とするNF3 ガスの前処理方法で、除去薬剤と
して酸化カルシウム、酸化マグネシウムの中から選ばれ
る少なくとも一種以上からなり、また除去薬剤として、
水酸化カルシウム、水酸化カリウム、水酸化ナトリウ
ム、水酸化マグネシウムの中から選ばれる一種以上およ
びゼオライト、シリカゲルから選ばれる一種以上との組
合せからなるNF3 ガスの前処理方法であり、さらに除
去部に設けた窓部に被除去成分と作用して変色する物質
を配することによって除去薬剤の寿命を検知する方法を
備え、また除去部の温度の上昇を感知することにより除
去薬剤の寿命を検知する方法を備えたNF3 ガスの前処
理方法である。[0009] The present invention, prior to the step of abating NF 3 gas, hydrogen bromide coexisting with NF 3 gas, hydrogen chloride, bromine, and wherein the reaction is removed using a chlorine removal agent In the pretreatment method for NF 3 gas, the removal agent comprises at least one selected from calcium oxide and magnesium oxide.
A method for pretreating NF 3 gas, which comprises a combination of one or more selected from calcium hydroxide, potassium hydroxide, sodium hydroxide and magnesium hydroxide and one or more selected from zeolite and silica gel. The window provided is provided with a method for detecting the life of the removed chemical by arranging a substance that changes color by acting on the component to be removed, and also detects the life of the removed chemical by detecting the temperature rise of the removal section. The method is a pretreatment method for NF 3 gas.
【0010】臭化水素等を除去する薬剤としては一般的
にはアルカリ薬剤として水酸化カルシウム、水酸化カリ
ウム、水酸化ナトリウム、水酸化マグネシウム等が知ら
れているが、該薬剤と臭化水素等との反応生成物である
水分は後段のNF3 除害装置にとっては大変具合いが悪
い。なぜなら、この水分はNF3 が分解して生成したF
原子との作用で高温の反応器の材質の金属を著しく腐食
するからである。As chemicals for removing hydrogen bromide and the like, calcium hydroxide, potassium hydroxide, sodium hydroxide, magnesium hydroxide and the like are generally known as alkaline chemicals. Moisture, which is a reaction product with, is very unsatisfactory for the NF 3 abatement device in the subsequent stage. Because this water is F generated by decomposition of NF 3.
This is because the action of the atoms significantly corrodes the metal of the high temperature reactor material.
【0011】本発明者らは臭化水素等の除去薬剤につい
て鋭意検討した結果、酸化カルシウム、酸化マグネシウ
ムの中から選ばれる少なくとも一種以上の薬剤が、かか
る目的に対して非常に有用であることを見いだし本発明
に至った。即ち酸化カルシウム、酸化マグネシウムの中
から選ばれた少なくとも一種以上の薬剤をNF3 除害装
置の前段に配置することにより臭化水素等がカルシウム
塩またはマグネシウム塩の形で反応固定され、かつ同時
に該反応で生成する水分は当該薬剤で吸収されるので、
後段のNF3 除害装置になんら悪影響を及ぼすことな
く、臭化水素等の予備処理を行うことができることを見
出した。As a result of intensive investigations by the present inventors on agents for removing hydrogen bromide and the like, it has been found that at least one agent selected from calcium oxide and magnesium oxide is very useful for this purpose. The present invention has been found out. That is, by disposing at least one or more agents selected from calcium oxide and magnesium oxide in the preceding stage of the NF 3 abatement device, hydrogen bromide and the like are reacted and fixed in the form of calcium salt or magnesium salt, and at the same time, Since the water generated by the reaction is absorbed by the drug,
It has been found that the pretreatment of hydrogen bromide or the like can be performed without any adverse effect on the NF 3 abatement device in the latter stage.
【0012】さらに反応によって水分が生じる水酸化カ
ルシウム、水酸化カリウム、水酸化ナトリウム、水酸化
マグネシウムにおいても、脱水剤であるゼオライトまた
はシリカゲルと組み合わせて用いることにより水分の影
響を排除でき臭化水素等の除去薬剤として充分用い得る
ということが分かった。即ち、前段に水酸化カルシウム
等、後段にゼオライト等という順序でガスを接触させる
ことでNF3 除害装置になんら悪影響を及ぼすことな
く、臭化水素等の予備処理を行うことができることを見
出した。Further, in the case of calcium hydroxide, potassium hydroxide, sodium hydroxide and magnesium hydroxide, which produce water by the reaction, the effect of water can be eliminated by using them in combination with zeolite or silica gel which is a dehydrating agent. It was found that it can be sufficiently used as a removing agent for That is, it was found that pretreatment of hydrogen bromide or the like can be carried out by contacting gases in the order of calcium hydroxide or the like in the first stage and zeolite or the like in the second stage without adversely affecting the NF 3 abatement device. .
【0013】さらにNF3 除害ラインに臭化水素等の流
入を継続させた場合、本発明が提供する臭化水素等の除
去薬剤によって処理できるとはいうものの、薬剤の能力
が有限であるからにはいずれ臭化水素等の除去能力は失
われるため、該薬剤寿命を未然に検知して操作員に知ら
しめる機構が必要である。Further, if hydrogen bromide or the like is continued to flow into the NF 3 abatement line, it can be treated by the agent for removing hydrogen bromide or the like provided by the present invention, but the capability of the agent is limited. Since the ability to remove hydrogen bromide and the like will eventually be lost, a mechanism is necessary to detect the life of the chemical and inform the operator.
【0014】本発明は当該検知機構についてもその方法
を提供するものである。即ち、臭化水素等の除去薬剤の
能力が失われてしまった場合にはその下流側に臭化水素
等が流出してくるのでこの臭化水素等を分析することに
よって対策を構じることができる。ただしこの場合、臭
化水素等の除去部の出口ガスを分析したのでは臭化水素
等を検出するのとその臭化水素等がNF3 除害反応部へ
流入するのが同時であるので未然に対処することができ
ない。臭化水素等の除去部の上流側の薬剤が能力を失っ
ても残りの下流側の薬剤が依然能力を保持しているよう
に臭化水素等の除去部の適切な位置に臭化水素等との反
応により変色する試薬を臭化水素等の除去部に外部から
観察できるようにして配する方法をも本発明で提供する
ところである。変色薬剤としては対象となる被除去成分
に応じて選択すればよく、例としてメチルオレンジ、ク
レゾールレッド、ベンゼンアゾジフェニルアミン、オル
トトリジン等が利用できる。変色試薬はシリカゲル、多
孔質アルミナ、ろ紙などの担体に付着させた形で利用す
ることができる。The present invention also provides a method for the detection mechanism. In other words, if the ability of a chemical agent for removing hydrogen bromide, etc. is lost, hydrogen bromide, etc. will flow out to the downstream side, so take measures by analyzing this hydrogen bromide, etc. You can However, in this case, if the outlet gas of the removal unit for hydrogen bromide, etc. is analyzed, it will occur at the same time that hydrogen bromide, etc. will be detected and that hydrogen bromide, etc. will flow into the NF 3 abatement reaction unit. Can't deal with. Even if the chemicals on the upstream side of the removal unit for hydrogen bromide lose their ability, the remaining chemicals on the downstream side still retain their ability. The present invention also provides a method of arranging a reagent that changes color due to the reaction with the above in a portion where hydrogen bromide or the like is removed so that it can be observed from the outside. The discoloring agent may be selected according to the target component to be removed, and examples thereof include methyl orange, cresol red, benzeneazodiphenylamine, orthotolidine and the like. The color-changing reagent can be used in the form of being attached to a carrier such as silica gel, porous alumina, or filter paper.
【0015】また、工程の無人化・自動化のため電気的
な信号により検知する方法も必要になり、本発明はその
ための方法をも提供するものである。即ち、酸化カルシ
ウム、酸化マグネシウム、水酸化カルシウム、水酸化カ
リウム、水酸化ナトリウム、水酸化マグネシウムはいず
れも臭化水素等との反応により発熱するため温度上昇を
センサーで捕らえることにより除去薬剤としての寿命を
検知することができる。例えば下部に温度センサーを配
した容器にこれら除去薬剤を充填し上方から臭化水素等
を含むガスを導入した場合、温度上昇によってセンサー
よりも上流側の除去薬剤が破過したということを知るこ
とができる。この温度センサーによって捉えられた信号
でランプ、ブザーなどの警報器を作動して操作員に危険
状態を迅速に知らしめることもできるし、また臭化水素
等の元バルブを自動的に閉止して危険状態の原因を絶つ
ことも可能である。上記のNF3 除害ラインへの臭化水
素等の流入検知機構においては、警報を出力する温度レ
ベルとしては正常状態での温度の変動幅に誤差の幅を加
えた値に設定するのが実用的である。In addition, a method of detecting with an electric signal is also required for unmanned / automated process, and the present invention also provides a method therefor. That is, calcium oxide, magnesium oxide, calcium hydroxide, potassium hydroxide, sodium hydroxide, magnesium hydroxide all generate heat due to reaction with hydrogen bromide, etc. Can be detected. For example, if a container with a temperature sensor at the bottom is filled with these removal agents and a gas containing hydrogen bromide is introduced from above, it is necessary to know that the removal agent on the upstream side of the sensor has breached due to the temperature rise. You can Signals captured by this temperature sensor can be used to activate alarm devices such as lamps and buzzers to promptly notify the operator of a dangerous condition, and the original valve for hydrogen bromide can be automatically closed. It is also possible to eliminate the cause of the dangerous condition. In the above-mentioned mechanism for detecting the inflow of hydrogen bromide or the like into the NF 3 abatement line, it is practical to set the temperature level at which the alarm is output to a value obtained by adding the error width to the temperature fluctuation width in the normal state. Target.
【0016】これら除去薬剤寿命を検知する変色指示装
置、温度上昇検出装置を設置する位置については、それ
らの信号を検出した後バックアップとして薬剤の余裕を
どれだけ確保しておけばよいかによって決まるため、シ
ステムの都合によって適宜設計すればよい。The positions of the discoloration indicating device and the temperature rise detecting device for detecting the lifespan of the removed chemicals are determined by how much margin of the chemicals should be secured as a backup after detecting these signals. It may be designed as appropriate according to the convenience of the system.
【0017】[0017]
【実施例】以下本発明を具体例によって説明する。 実施例1 両端にガスの出入口と、長手方向に100mm置きに4
本の熱電対を内部に備えた内径70mm、長さ500m
mのステンレス容器を臭化水素等の除去カラムとし、出
口部にガスサンプリングスタンドを設けた。該除去カラ
ムにCaO(径3〜5mm)を2Kg充填し垂直に固定
し室温状態で上方の口からNF3 =10%、残部N2 の
混合ガスを1000cc/minの流量で流し除去カラ
ム出口のガスを分析したところ、NF3 =10%であり
変化はなかった。またカラム内の温度にも変化はなかっ
た。EXAMPLES The present invention will be described below with reference to specific examples. Example 1 A gas inlet / outlet is provided at both ends, and a gas is placed every 100 mm in the longitudinal direction.
70 mm inside diameter, 500 m long with a thermocouple inside
A stainless steel container of m was used as a column for removing hydrogen bromide and the like, and a gas sampling stand was provided at the outlet. 2 Kg of CaO (diameter 3 to 5 mm) was packed in the removal column and fixed vertically, and at room temperature, NF 3 = 10% and the balance gas of N 2 were flowed at a flow rate of 1000 cc / min from the upper port, and at the outlet of the removal column. When the gas was analyzed, NF 3 = 10%, which was unchanged. There was also no change in the temperature inside the column.
【0018】ついでNF3 =10%、HBr=10%、
残部N2 の混合ガスを1000cc/minの流量で流
し出口ガスを分析したところ、NF3 =11%、HBr
<1ppm(検出下限以下)、H2 O<3μg/lであ
った。内部の温度はガス入口付近が最も高く54℃に達
した(実験開始前 20℃)。Then, NF 3 = 10%, HBr = 10%,
When the mixed gas of the balance N 2 was flowed at a flow rate of 1000 cc / min and the outlet gas was analyzed, NF 3 = 11%, HBr
<1 ppm (below the lower limit of detection) and H 2 O <3 μg / l. The temperature inside was highest near the gas inlet and reached 54 ° C (20 ° C before the start of the experiment).
【0019】供給したHBrの積算値が200gになっ
た時点で出口ガスの組成はNF3 =11%、HBr<1
ppm(検出下限以下)、H2 O<3μg/lであっ
た。また内部の温度はガス出口付近が最も高く50℃に
達した。When the integrated value of the supplied HBr reaches 200 g, the composition of the outlet gas is NF 3 = 11%, HBr <1.
ppm (below the lower limit of detection), H 2 O <3 μg / l. The internal temperature reached 50 ° C, which was the highest near the gas outlet.
【0020】供給したHBrの積算値が220gになっ
た時点で出口ガスの組成はNF3 =11%、HBr<1
ppm(検出下限以下)、H2 O=20μg/lであっ
た。供給したHBrの積算値が260gになった時点で
出口ガスの組成はNF3 =11%、HBr=10pp
m、H2 O=150μg/lであった。When the integrated value of the supplied HBr reaches 220 g, the composition of the outlet gas is NF 3 = 11%, HBr <1.
ppm (below the lower limit of detection), H 2 O = 20 μg / l. When the integrated value of the supplied HBr reached 260 g, the composition of the outlet gas was NF 3 = 11%, HBr = 10 pp.
m, H 2 O = 150 μg / l.
【0021】実施例2 NF3 =10%、HCl=10%、残部N2 の混合ガス
である以外は実施例1と同様な実験を行い出口ガスを分
析したところ、NF3 =11%、HCl<1ppm(検
出下限以下)、H2 O<3μg/lであった。内部の温
度はガス入口付近が最も高く58℃に達した(実験開始
前 20℃)。Example 2 The same experiment as in Example 1 was carried out except that a mixed gas of NF 3 = 10%, HCl = 10% and the balance N 2 was used, and the outlet gas was analyzed. NF 3 = 11%, HCl <1 ppm (below the lower limit of detection) and H 2 O <3 μg / l. The highest internal temperature reached 58 ° C near the gas inlet (20 ° C before the start of the experiment).
【0022】供給したHClの積算値が70gになった
時点で出口ガスの組成はNF3 =11%、HCl<1p
pm(検出下限以下)、H2 O<3μg/lであった。
また内部の温度はガス出口付近が最も高く53℃に達し
た。When the integrated value of the supplied HCl reached 70 g, the composition of the outlet gas was NF 3 = 11%, HCl <1 p
pm (below the lower limit of detection), H 2 O <3 μg / l.
The internal temperature reached 53 ° C, which was the highest near the gas outlet.
【0023】供給したHClの積算値が80gになった
時点で出口ガスの組成はNF3 =11%、HCl<1p
pm(検出下限以下)、H2 O=30μg/lであっ
た。供給したHClの積算値が100gになった時点で
出口ガスの組成はNF3 =11%、HCl=20pp
m、H2 O=200μg/lであった。When the integrated value of the supplied HCl reached 80 g, the composition of the outlet gas was NF 3 = 11%, HCl <1 p
pm (below the lower limit of detection), H 2 O = 30 μg / l. When the integrated value of the supplied HCl reached 100 g, the composition of the outlet gas was NF 3 = 11%, HCl = 20 pp.
m, H 2 O = 200 μg / l.
【0024】実施例3 NF3 =10%、Br2 =10%、残部N2 の混合ガス
である以外は実施例1と同様な実験を行い出口ガスを分
析したところ、NF3 =11%、Br2 <1ppm(検
出下限以下)、H2 O<3μg/lであった。内部の温
度はガス入口付近が最も高く47℃に達した(実験開始
前 20℃)。Example 3 The same experiment as in Example 1 was carried out except that the mixed gas was NF 3 = 10%, Br 2 = 10%, and the balance was N 2 , and the outlet gas was analyzed. NF 3 = 11%, Br 2 <1 ppm (below the lower limit of detection) and H 2 O <3 μg / l. The internal temperature reached 47 ° C, the highest near the gas inlet (20 ° C before the start of the experiment).
【0025】供給したBr2 の積算値が70gになった
時点で出口ガスの組成はNF3 =11%、Br2 <1p
pm(検出下限以下)、H2 O<3μg/lであった。
また内部の温度はガス出口付近が最も高く45℃に達し
た。When the integrated value of Br 2 supplied reached 70 g, the composition of the outlet gas was NF 3 = 11%, Br 2 <1 p.
pm (below the lower limit of detection), H 2 O <3 μg / l.
The internal temperature reached 45 ° C, which was the highest near the gas outlet.
【0026】供給したBr2 の積算値が80gになった
時点で出口ガスの組成はNF3 =11%、Br2 =50
ppm、H2 O<3μg/lであった。 実施例4 NF3 =10%、Cl2 =10%、残部N2 の混合ガス
である以外は実施例1と同様な実験を行い出口ガスを分
析したところ、NF3 =11%、Cl2 <1ppm(検
出下限以下)、H2 O<3μg/lであった。内部の温
度はガス入口付近が最も高く58℃に達した(実験開始
前 20℃)。When the integrated value of Br 2 supplied reached 80 g, the composition of the outlet gas was NF 3 = 11% and Br 2 = 50.
ppm, H 2 O <3 μg / l. Example 4 The same experiment as in Example 1 was carried out except that a mixed gas of NF 3 = 10%, Cl 2 = 10% and the balance of N 2 was used, and the outlet gas was analyzed. NF 3 = 11%, Cl 2 < It was 1 ppm (below the lower limit of detection) and H 2 O <3 μg / l. The highest internal temperature reached 58 ° C near the gas inlet (20 ° C before the start of the experiment).
【0027】供給したCl2 の積算値が30gになった
時点で出口ガスの組成はNF3 =11%、Cl2 <1p
pm(検出下限以下)、H2 O<3μg/lであった。
また内部の温度はガス出口付近が最も高く53℃に達し
た。At the time when the integrated value of the supplied Cl 2 reached 30 g, the composition of the outlet gas was NF 3 = 11%, Cl 2 <1 p.
pm (below the lower limit of detection), H 2 O <3 μg / l.
The internal temperature reached 53 ° C, which was the highest near the gas outlet.
【0028】供給したCl2 の積算値が40gになった
時点で出口ガスの組成はNF3 =11%、Cl2 =40
ppm、H2 O<3μg/lであった。 実施例5 実施例1の該カラムのガス出口付近に石英製の窓を設け
窓の内側にベンゼンアゾジフェニルアミンをシリカゲル
に担持した粒子(黄色)を配した。そのほかの条件は実
施例1と同様に実験を行ったところ、供給したHBrの
積算値が200gになった時点で該粒子の色が黄色から
赤色に変化し、薬剤が破過しHBrが検出されたことを
示した。When the integrated value of the supplied Cl 2 reached 40 g, the composition of the outlet gas was NF 3 = 11%, Cl 2 = 40.
ppm, H 2 O <3 μg / l. Example 5 A window made of quartz was provided near the gas outlet of the column of Example 1, and particles (yellow) in which benzeneazodiphenylamine was supported on silica gel were arranged inside the window. Other conditions were tested in the same manner as in Example 1, and at the time when the integrated value of the supplied HBr reached 200 g, the color of the particles changed from yellow to red, the drug broke through, and HBr was detected. I showed that.
【0029】実施例6 供給ガスNF3 =10%、HBr=5%、残部N2 の混
合ガスである以外は実施例1と同様な実験を行ったとこ
ろ、供給したHBrの積算値が200gになった時点で
カラム内温度がガス出口付近で最高41℃(初期20
℃)となり除去薬剤全量が破過したことが分かった。Example 6 The same experiment as in Example 1 was carried out except that the mixed gas of the supply gas NF 3 = 10%, HBr = 5%, and the balance N 2 was carried out, and the integrated value of the supplied HBr was 200 g. The temperature inside the column reached a maximum of 41 ° C near the gas outlet (initial 20
It was found that the total amount of the removed chemicals passed through.
【0030】実施例7 CaOの代わりにMgO(径3〜5mm)を2Kg充填
する以外は実施例1と同様な実験を行った。出口ガスを
分析したところ、NF3 =11%、HBr<1ppm
(検出下限以下)、H2 O<3μg/lであった。Example 7 The same experiment as in Example 1 was conducted except that 2 kg of MgO (diameter: 3 to 5 mm) was filled instead of CaO. Analysis of the outlet gas showed that NF 3 = 11%, HBr <1 ppm
(Below the lower limit of detection), H 2 O <3 μg / l.
【0031】実施例8 CaOの代わりにCa(OH)2 (径3〜5mm)を1
Kg、ゼオライト(3A)を1Kg充填する以外は実施
例1と同様な実験を行った。出口ガスを分析したとこ
ろ、NF3 =11%、HBr<1ppm(検出下限以
下)、H2 O<3μg/lであった。Example 8 1% Ca (OH) 2 (diameter 3-5 mm) was used instead of CaO.
The same experiment as in Example 1 was conducted except that 1 kg of Kg and 1 kg of zeolite (3A) were charged. When the outlet gas was analyzed, NF 3 = 11%, HBr <1 ppm (below the lower limit of detection), and H 2 O <3 μg / l.
【0032】実施例9 CaOの代わりにMg(OH)2 (径3〜5mm)を1
Kg、ゼオライト(3A)を1Kg充填する以外は実施
例1と同様な実験を行った。出口ガスを分析したとこ
ろ、NF3 =11%、HBr<1ppm(検出下限以
下)、H2 O<3μg/lであった。Example 9 1% of Mg (OH) 2 (diameter 3-5 mm) was used instead of CaO.
The same experiment as in Example 1 was conducted except that 1 kg of Kg and 1 kg of zeolite (3A) were charged. When the outlet gas was analyzed, NF 3 = 11%, HBr <1 ppm (below the lower limit of detection), and H 2 O <3 μg / l.
【0033】実施例10 内径400mm長さ960mmの除去カラムにCaOを
75kg充填し、さらに出口配管の下流側に金属シリコ
ンを充填したNi製反応器(ヒーターで600℃に加
熱)からなるNF3 除害装置を結合した。Example 10 NF 3 removal consisting of a Ni reactor (heated to 600 ° C. with a Ni) in which a removal column having an inner diameter of 400 mm and a length of 960 mm was filled with 75 kg of CaO and metal silicon was filled in the downstream side of the outlet pipe. Combined harm device.
【0034】除去カラム入口からNF3 =1%、HBr
=1%、残部N2 の混合ガスを10l/minの流量で
流しNF3 除害装置の出口ガスを分析したところ、NF
3 <10ppm、SiF4 =0.75%、HBr<1p
pm(検出下限以下)、H2O<3μg/lであった。
120時間連続処理した後NF3 除害装置を解体し反応
器内部を観察したところ腐食は全く生じていなかった。From the removal column inlet, NF 3 = 1%, HBr
= 1% and the balance N 2 mixed gas was flowed at a flow rate of 10 l / min, and the outlet gas of the NF 3 abatement device was analyzed.
3 <10ppm, SiF 4 = 0.75 %, HBr <1p
pm (below the lower limit of detection), H 2 O <3 μg / l.
After continuously treating for 120 hours, the NF 3 abatement device was disassembled and the inside of the reactor was observed, and no corrosion occurred.
【0035】比較例 CaOの代わりにCa(OH)2 (径3〜5mm)を2
Kg充填する以外は実施例1と同様な実験を行った。出
口ガスを分析したところ、NF3 =11%、HBr<1
ppm(検出下限以下)、H2 O=40mg/lであ
り、HBrの除去は認められたが、H2 Oが検出され
た。Comparative Example 2 Ca (OH) 2 (diameter 3-5 mm) was used instead of CaO 2.
The same experiment as in Example 1 was performed except that Kg was charged. Analysis of the outlet gas showed that NF 3 = 11%, HBr <1
ppm (below the lower limit of detection), H 2 O = 40 mg / l, removal of HBr was recognized, but H 2 O was detected.
【0036】[0036]
【発明の効果】本発明により、NF3 ガスと共存する臭
化水素等を予め前処理除去することが可能となりNF3
ガス除害装置の安全な保守管理を行うことができ、NF
3 ガスをより安全に除害できる。Effect of the Invention] The present invention, NF 3 it is possible to pre-preprocessing removes the hydrogen bromide or the like to coexist with NF 3 gas
Safe maintenance management of gas abatement equipment can be performed, and NF
3 Gas can be removed more safely.
Claims (5)
F3 ガスと共存している臭化水素、塩化水素、臭素、塩
素を除去薬剤を用いて反応除去することを特徴とするN
F3 ガスの前処理方法。1. Prior to the step of removing NF 3 gas, N
N characterized by reacting and removing hydrogen bromide, hydrogen chloride, bromine and chlorine coexisting with F 3 gas using a removing agent
Pretreatment method for F 3 gas.
グネシウムの中から選ばれる少なくとも一種以上からな
る請求項1記載のNF3 ガスの前処理方法。2. The pretreatment method for NF 3 gas according to claim 1, which comprises at least one selected from calcium oxide and magnesium oxide as a removing agent.
酸化カリウム、水酸化ナトリウム、水酸化マグネシウム
の中から選ばれる一種以上およびゼオライト、シリカゲ
ルから選ばれる一種以上との組合せからなる請求項1記
載のNF3 ガスの前処理方法。3. The removing agent according to claim 1, which comprises a combination of one or more selected from calcium hydroxide, potassium hydroxide, sodium hydroxide and magnesium hydroxide and one or more selected from zeolite and silica gel. Pretreatment method for NF 3 gas.
して変色する物質を配することによって除去薬剤の寿命
を検知する方法を備えた請求項1記載のNF3 ガスの前
処理方法。4. The pretreatment of NF 3 gas according to claim 1, further comprising a method for detecting the life of the removed chemical by disposing a substance that changes color by acting on a component to be removed in a window provided in the removing section. Method.
り除去薬剤の寿命を検知する方法を備えた請求項1記載
のNF3 ガスの前処理方法。5. The NF 3 gas pretreatment method according to claim 1, further comprising a method of detecting the life of the removed chemical by detecting an increase in the temperature of the removal section.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP23451692A JP3264453B2 (en) | 1992-09-02 | 1992-09-02 | NF 3 gas pretreatment method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP23451692A JP3264453B2 (en) | 1992-09-02 | 1992-09-02 | NF 3 gas pretreatment method |
Publications (2)
Publication Number | Publication Date |
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JPH0679138A true JPH0679138A (en) | 1994-03-22 |
JP3264453B2 JP3264453B2 (en) | 2002-03-11 |
Family
ID=16972254
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JP23451692A Expired - Fee Related JP3264453B2 (en) | 1992-09-02 | 1992-09-02 | NF 3 gas pretreatment method |
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6562748B2 (en) * | 1996-10-17 | 2003-05-13 | Intersurgical Limited | Process for the manufacture of chemical absorbents and chemical absorbent formulations |
JP2006172411A (en) * | 2004-12-17 | 2006-06-29 | Sgt Singapore Holdings Pte Ltd | Decompression device with display device and component instrument kit consisting of display device for decompression device and gas source |
JP2009034671A (en) * | 2007-07-10 | 2009-02-19 | Ebara Corp | Treatment apparatus of perfluoro compound (pfc) and treatment method of pfc-containing gas |
JP2010158620A (en) * | 2009-01-08 | 2010-07-22 | Ebara Corp | Method of treating emission comprising fluorine-containing compound, and reaction vessel for treating emission |
TWI454305B (en) * | 2007-07-10 | 2014-10-01 | Ebara Corp | Fluorine fixing agent and pfc decomposition treatment agent and preparing methods for the same, pfc processing apparatus and processing method for pfc-containing gas |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2009008454A1 (en) * | 2007-07-10 | 2009-01-15 | Ebara Corporation | Fluorine-fixing agent, pfc-decomposing/treating agent, and methods for preparation of the fluorine-fixing agent and the pfc-decomposing/treating agent |
-
1992
- 1992-09-02 JP JP23451692A patent/JP3264453B2/en not_active Expired - Fee Related
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6562748B2 (en) * | 1996-10-17 | 2003-05-13 | Intersurgical Limited | Process for the manufacture of chemical absorbents and chemical absorbent formulations |
JP2006172411A (en) * | 2004-12-17 | 2006-06-29 | Sgt Singapore Holdings Pte Ltd | Decompression device with display device and component instrument kit consisting of display device for decompression device and gas source |
JP2009034671A (en) * | 2007-07-10 | 2009-02-19 | Ebara Corp | Treatment apparatus of perfluoro compound (pfc) and treatment method of pfc-containing gas |
TWI454305B (en) * | 2007-07-10 | 2014-10-01 | Ebara Corp | Fluorine fixing agent and pfc decomposition treatment agent and preparing methods for the same, pfc processing apparatus and processing method for pfc-containing gas |
JP2010158620A (en) * | 2009-01-08 | 2010-07-22 | Ebara Corp | Method of treating emission comprising fluorine-containing compound, and reaction vessel for treating emission |
Also Published As
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JP3264453B2 (en) | 2002-03-11 |
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