JPH0741145B2 - Etching exhaust gas removal method - Google Patents
Etching exhaust gas removal methodInfo
- Publication number
- JPH0741145B2 JPH0741145B2 JP61282094A JP28209486A JPH0741145B2 JP H0741145 B2 JPH0741145 B2 JP H0741145B2 JP 61282094 A JP61282094 A JP 61282094A JP 28209486 A JP28209486 A JP 28209486A JP H0741145 B2 JPH0741145 B2 JP H0741145B2
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- JP
- Japan
- Prior art keywords
- exhaust gas
- etching exhaust
- heat
- packed bed
- heat generation
- Prior art date
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Description
【発明の詳細な説明】 [産業上の利用分野] 本発明は、エッチング排ガスの除害方法に関するもので
ある。TECHNICAL FIELD The present invention relates to a method of removing etching exhaust gas.
[従来の技術] 従来より半導体産業を中心に、毒性、腐蝕性ガスを除去
する除害装置が利用されている。[Prior Art] Conventionally, an abatement device for removing toxic and corrosive gases has been used mainly in the semiconductor industry.
しかしながら、化学反応剤、吸着薬剤は除害ガスによ
り、それぞれの能力に応じ無効力化、飽和してしまうた
め連続処理をしていると有害ガスが透過(破過)してま
う恐れがある。このため破過を事前に検知する必要があ
り、公知の技術としては吸着ガス量を重量により測定し
て破過を検知する方法(特開昭61-68536号公報参照)、
反応試薬による呈色反応により破過を検知する方法が知
られている。However, the chemical reaction agent and the adsorbing agent are deactivated and saturated depending on their respective capacities by the detoxifying gas, so that the harmful gas may permeate (break through) during continuous treatment. Therefore, it is necessary to detect breakthrough in advance, and as a known technique, a method of measuring the amount of adsorbed gas by weight to detect breakthrough (see JP-A-61-68536),
A method of detecting breakthrough by a color reaction with a reaction reagent is known.
[発明の解決しようとする問題点] 従来の重量法では、同種薬剤であってもその経歴等によ
り処理できるガス量が異なるため正確に破過を検知でき
ない欠点があった。また水分などの混入による薬剤等の
異常発熱は重量法では検知できない。呈色反応を用いる
方法では、検知をどうしても人の目にたよらざるを得な
いため装置の自動化は、むずかしい。又、異常発熱の検
知はできない。これらの欠点をなくし、正確に異常発熱
と破過を検知する目的で本発明は成された。[Problems to be Solved by the Invention] The conventional gravimetric method has a drawback that the breakthrough cannot be accurately detected because the amount of gas that can be processed varies depending on the history of the same kind of drug. Further, the abnormal heat generation of the drug or the like due to the mixing of water or the like cannot be detected by the gravimetric method. In the method using the color reaction, it is difficult to automate the device because the detection is inevitably invisible to human eyes. Also, abnormal heat generation cannot be detected. The present invention was made for the purpose of eliminating these drawbacks and accurately detecting abnormal heat generation and breakthrough.
[問題点を解決するための手段] 本発明は、前述の問題点を解決すべくなされたものであ
り、ハロゲンまたはハロゲン化合物と化学反応してこれ
らを定着することのできる化学反応剤を含む充填層に、
ハロゲンまたはハロゲン化合物を含むエッチング排ガス
を導入して除害する方法であって、エッチング排ガス出
口近傍に熱検出器を設け、エッチング排ガスと化学反応
剤の反応熱による温度上昇、および、充填層に導入され
る水分と化学反応剤との反応による異常発熱による温度
上昇を測定し、異常発熱による温度上昇が反応熱による
温度上昇より高いことを利用して、異常発熱と充填層の
破過とを区別して検知するエッチング排ガス除害方法を
提供するものである。[Means for Solving the Problems] The present invention has been made to solve the above-mentioned problems, and a filling containing a chemical reaction agent capable of chemically reacting with halogen or a halogen compound to fix these. In layers,
This is a method of introducing and removing the etching exhaust gas containing halogen or halogen compounds, in which a heat detector is installed near the etching exhaust gas outlet to raise the temperature due to the reaction heat of the etching exhaust gas and the chemical reactant, and to introduce it into the packed bed. The temperature rise due to the abnormal heat generation due to the reaction between the water and the chemical reaction agent is measured, and the fact that the temperature rise due to the abnormal heat generation is higher than the temperature rise due to the reaction heat is used to distinguish the abnormal heat generation from the breakthrough of the packed bed. The present invention provides a method of removing etching exhaust gas that is separately detected.
近年の半導体の高集積にともない微細加工技術の進歩が
著しい。特に微細パターンを作成するためにハロゲン化
合物を用いたドライエッチング技術が頻繁に使用されて
いる。しかし、ドライエッチング排ガス中にはBCl3,CCl
4,Cl2,SiCl4,HCl,COCl2,F2,COF2,HF等の毒性、腐蝕性を
有するハロゲンあるいはハロゲン化合物のガスが含まれ
ており、これらのガスをエッチング装置ごとに除去する
ことが望ましい。本発明はこれらのガスを除害する際に
化学反応剤を含む充填層とエッチング排ガスとの化学反
応熱や吸着熱を熱検出器で検知することで除害装置の破
過及び異常発熱を予め検知する方法であり、事前に当該
装置において別の手段を用いて破過を検出し、そのとき
の温度を記録しておくのが好ましい。With the recent high integration of semiconductors, the progress of fine processing technology is remarkable. Particularly, a dry etching technique using a halogen compound is frequently used to form a fine pattern. However, BCl 3 and CCl are contained in the dry etching exhaust gas.
4, Cl 2, SiCl 4, HCl, COCl 2, F 2, COF 2, toxicity such as HF, includes a gas halogens or halogen compounds having corrosion resistance, removing these gases per etching apparatus Is desirable. The present invention detects breakthrough and abnormal heat generation of the abatement device in advance by detecting the heat of chemical reaction or the heat of adsorption between the packed bed containing the chemical reactant and the etching exhaust gas when removing these gases with a heat detector. It is a method of detecting, and it is preferable to detect the breakthrough using another means in the apparatus in advance and record the temperature at that time.
添付第1図に、本発明で用いる装置の典型的な一例であ
る断面図を示す。エッチング排ガスは装置入口1からPT
FE(ポリテトラフルオロエチレン)製インサート管2を
通って、充填層3を上昇し、無害化されて装着出口4か
ら排出される。充填容器の外壁5や内壁6は前記化学反
応熱による充填層内の発熱帯域が狭くなるように、熱伝
導率が小さいことが望ましく、又、内壁6は腐蝕性排ガ
スに耐えるものが望ましいことから、外壁として合成樹
脂、特に繊維強化合成樹脂(FRP)を、又内壁としてPTF
Eを採用することが好ましい。FIG. 1 attached herewith shows a cross-sectional view of a typical example of the apparatus used in the present invention. Etching exhaust gas is PT from the equipment inlet 1.
After passing through the insert tube 2 made of FE (polytetrafluoroethylene), the packed bed 3 rises, is rendered harmless, and is discharged from the mounting outlet 4. It is desirable that the outer wall 5 and the inner wall 6 of the filling container have a small thermal conductivity so that the heat generation zone in the filling layer due to the heat of the chemical reaction is narrowed, and the inner wall 6 is preferably one that can withstand corrosive exhaust gas. , Synthetic resin as outer wall, especially fiber reinforced synthetic resin (FRP), and inner wall as PTF
It is preferable to adopt E.
充填層3のエッチング排ガス出口近傍に設ける熱検出器
としては、感熱紙等の目視で判断できるものでもよい
が、検知後、外部に信号出力が可能である熱電対、バイ
メタル、オイル等の熱媒体の熱膨張、赤外線、溶断ヒュ
ーズ等を用いたものが有効である。熱検出器の設置場所
は、充填層内のエッチング排ガス出口近傍(第1図の
7)でもよく、充填層のエッチング排ガス出口近傍の充
填容器内壁あるいは外壁であってもよい。充填層内に設
置する場合には、PTFE等で耐蝕対策を施した熱検出器と
することが好ましい。熱検出器の設置位置を排ガス出口
に近づければ破過の直前に検知でき、遠ざければより速
い時期に破過を予測できる。As the heat detector provided in the vicinity of the etching exhaust gas outlet of the packed bed 3, a heat-sensitive paper or the like that can be visually determined may be used, but after detection, a heat medium such as a thermocouple, bimetal, or oil that can output a signal to the outside. It is effective to use thermal expansion, infrared rays, a blow fuse, or the like. The location of the heat detector may be in the vicinity of the etching exhaust gas outlet in the packed bed (7 in FIG. 1) or in the inner wall or outer wall of the packing container near the etching exhaust gas outlet of the packed bed. When it is installed in the packed bed, it is preferable to use a heat detector with corrosion resistance such as PTFE. If the installation position of the heat detector is close to the exhaust gas outlet, it can be detected immediately before the breakthrough, and if it is far away, the breakthrough can be predicted earlier.
化学反応剤としては、アルカリ土類金属の酸化物、水酸
化物、ケイ酸塩、あるいは炭酸塩、アルカリ金属の炭酸
塩又は鉄族、クロム族元素等の酸化物が好ましい。具体
的には酸化マグネシウム、水酸化マグネシウム、炭酸マ
グネシウム、塩基性炭酸マグネシウム、酸化カルシウ
ム、ケイ酸カルシウム、炭酸ナトリウム、重炭酸ナトリ
ウム、酸化鉄、酸化クロム等である。これらは、2種以
上同時に使用してもよい。化学反応剤だけでなく、吸着
剤を併用することもできる。吸着剤としては、活性炭、
活性アルミナ、シリカゲル、ゼオライト等が好ましく、
これらも2種以上同時に使用し得る。As the chemical reactant, oxides, hydroxides, silicates, or carbonates of alkaline earth metals, carbonates of alkali metals, or oxides of iron group, chromium group elements or the like are preferable. Specifically, magnesium oxide, magnesium hydroxide, magnesium carbonate, basic magnesium carbonate, calcium oxide, calcium silicate, sodium carbonate, sodium bicarbonate, iron oxide, chromium oxide and the like. You may use these 2 or more types simultaneously. Not only the chemical reaction agent but also an adsorbent can be used together. As the adsorbent, activated carbon,
Activated alumina, silica gel, zeolite and the like are preferable,
Two or more of these may also be used simultaneously.
一般に、吸着剤による吸着熱は化学反応剤による反応熱
に比べ、発熱が小さいため、充填層に吸着剤を併用する
場合には、吸着剤と化学反応剤を混合したり、あるい
は、熱検出器設置位置付近の充填層には集中して化学反
応剤を充填するのが好ましい。熱検出器により、吸着熱
や反応熱の発熱を検知しやすくするためには、発熱量が
大きいこと、充填層内の発熱帯域が狭くなるように吸着
性や反応性が優れていることが重要であり、そのような
吸着剤や化学反応剤の種類又はこれらの組み合せを選択
することが好ましい。In general, the heat of adsorption from an adsorbent is smaller than the heat of reaction from a chemical reactant, so when using an adsorbent in a packed bed, the adsorbent and the chemical reactant may be mixed or a heat detector may be used. It is preferable to concentrate the chemical reaction agent in the packed bed near the installation position in a concentrated manner. In order to make it easier to detect the heat of adsorption heat or reaction heat with a heat detector, it is important that the heat generation amount is large and that the adsorption and reactivity are excellent so that the heat generation zone in the packed bed is narrowed. It is preferable to select the type of such adsorbent or chemical reaction agent or a combination thereof.
[作用] 本発明は排ガスの除害において破過時期を正確に検知で
きるとともに、自動的に破過警報を発することを可能と
した特徴を有している。これは排ガスが除害装置を通過
する際、排ガスが化学反応剤により発熱を伴ないながら
除害され、さらにこの発熱が定常運転において装置全体
に生じるものでなく、化学反応が生じている部分のみで
発熱し、この発熱帯域が排ガスの累積通過量の増加に従
い排ガスの流れに対し上流部から下流部へ徐々に移動す
るからである。すなわち、この発熱帯域より上流側の充
填剤は既に破過している状態であり熱検出器を充填層の
最下流に設置すれば除害装置の破過を検知することがで
きる。[Operation] The present invention has a feature that it is possible to accurately detect the breakthrough time in removing exhaust gas and to automatically issue a breakthrough alarm. This is because when the exhaust gas passes through the abatement device, the exhaust gas is removed by the chemical reaction agent while generating heat, and this heat generation does not occur in the entire device in steady operation, only the part where the chemical reaction occurs. This is because heat is generated in the heat generation zone, and this heat generation zone gradually moves from the upstream portion to the downstream portion with respect to the flow of the exhaust gas as the cumulative passage amount of the exhaust gas increases. That is, the filler on the upstream side of the heat generation zone has already passed through, and if the heat detector is installed at the most downstream side of the packed bed, the breakthrough of the abatement device can be detected.
この発明帯域の幅は化学反応剤の反応性能によって異な
り、反応性が高いもの程すみやかに反応が完結し発熱帯
域が狭くなる。すなわち、破過検知感度が高くなる。さ
らに本発明においては、多量の水分が除害装置に導入さ
れ充填剤に異常発熱が生じるような場合でも、破過と区
別して検知できる。これは、このような異常発熱量が定
常運転時のハロゲンまたはハロゲン化合物と化学反応剤
との反応熱とは比較にならない程大きく、熱が通過ガス
に同伴され装置全体の温度が上昇し、その上昇温度が定
常時の反応又は吸着による発熱上昇温度に比べ十分大き
いことにより、破過時と区別して検知できるからであ
る。The width of the invention zone depends on the reaction performance of the chemical reaction agent, and the higher the reactivity, the faster the reaction is completed and the narrower the exothermic zone. That is, the breakthrough detection sensitivity is increased. Further, in the present invention, even when a large amount of water is introduced into the detoxification device and the filler causes abnormal heat generation, it can be detected separately from breakthrough. This is because such an abnormal heating value is so large that it cannot be compared with the heat of reaction between the halogen or the halogen compound and the chemical reactant during steady operation, and the heat is entrained in the passing gas to raise the temperature of the entire device. This is because when the temperature rise is sufficiently higher than the temperature rise temperature due to reaction or adsorption during steady state, it can be detected separately from breakthrough.
[実施例] 「破過検知の実施例」 試験のために用いた試薬は次のものである。粒径2〜3m
mのMgO,Mg(OH)2,CaO,Na2CO3,Fe2O3,FeO、粒径4〜6mmの
活性炭、窒素中にF2を0.5vol%(以下の%はすべてvol
%である)含む混合ガス、窒素中にBCl3を2%含む混合
ガス、窒素中にHClを1%含む混合ガス、窒素中にCl2を
1%含む混合ガス、窒素中にHFを1%含む混合ガス、窒
素中にSiCl4を1%含む混合ガス。試験に用いた除害装
置は、内径350mm、高さ1030mmのPTFEライニングFRP管で
ある。[Example] "Example of breakthrough detection" The reagents used for the test are as follows. Particle size 2-3m
MgO, Mg (OH) 2 , CaO, Na 2 CO 3 , Fe 2 O 3 , FeO of m, activated carbon with a particle size of 4-6 mm, 0.5 vol% of F 2 in nitrogen (all the following% are vol
%) Mixed gas, mixed gas containing 2% BCl 3 in nitrogen, mixed gas containing 1% HCl in nitrogen, mixed gas containing 1% Cl 2 in nitrogen, 1% HF in nitrogen A mixed gas containing 1% SiCl 4 in nitrogen. The abatement device used in the test was a PTFE-lined FRP tube having an inner diameter of 350 mm and a height of 1030 mm.
実施例1,3,7,9,11においては、それぞれMgOを800mm層厚
さとなるように充填してF2/N2混合ガス、BCl2/N2混合ガ
ス、HCl/N2混合ガス、HF/N2ガス、SiCl4混合ガスを毎分
10l(室温25℃)で下部より流して試験した。温度測定
はクロメルーアルメル熱電対を充填層高さ680mmの位置
の除害装置外壁に貼付けて行なった。In Examples 1,3,7,9,11, respectively, MgO is filled so as to have a layer thickness of 800 mm, F 2 / N 2 mixed gas, BCl 2 / N 2 mixed gas, HCl / N 2 mixed gas, HF / N 2 gas, SiCl 4 mixed gas every minute
The test was carried out by flowing from the bottom with 10 l (room temperature 25 ° C). The temperature was measured by attaching a chromel-alumel thermocouple to the outer wall of the abatement system at a packed bed height of 680 mm.
実施例5においては、活性炭を800mm層厚さとなるよう
に充填して、Cl2/N2混合ガスを毎分10l(室温25℃)で
下部より流して試験した。温度測定は前述と同様な方法
で行なった。本実施例は、実施例4との比較のために行
ったもので、本発明には含まれない。In Example 5, activated carbon was filled so as to have a layer thickness of 800 mm, and a Cl 2 / N 2 mixed gas was flown from the bottom at a rate of 10 l / min (room temperature 25 ° C.) for testing. The temperature was measured by the same method as described above. This example was carried out for comparison with Example 4, and is not included in the present invention.
実施例2,10,12においては、それぞれMgOを下から650mm,
その上にCaOを50mm更にその上にMgOを100mm、計800mmの
厚さとなるように充填したものを用いた。それにそれぞ
れF2/N2、HF/N2、SiCl4/N2混合ガスを毎分10l(室温25
℃)で下部より流して試験を行なった。温度測定は前述
と同様な方法で行なった。In Examples 2, 10 and 12, MgO from the bottom 650 mm,
On top of that, CaO was filled in 50 mm, MgO was further filled in 100 mm, and the total thickness was 800 mm. Each of them was mixed with F 2 / N 2 , HF / N 2 and SiCl 4 / N 2 gas at a rate of 10 l / min (room temperature 25
The test was conducted by pouring from the bottom at (° C). The temperature was measured by the same method as described above.
実施例4においては、MgOを下から650mm,その上にNa2CO
3を50mm、更にその上にMgO100mm、計800mmの厚さとなる
ように充填したものを用いた。それにBCl2/N2混合ガス
を毎分10l(室温25℃)で下部より流して試験を行なっ
た。温度測定は前述と同様な方法で行なった。実施例5
と比較して測定温度が高く、破過がより容易に検出でき
た。In Example 4, MgO was 650 mm from the bottom and Na 2 CO was deposited on top of it.
3 was filled with 50 mm, MgO 100 mm, and a total thickness of 800 mm were used. BCl 2 / N 2 mixed gas was flown from the bottom at 10 l / min (room temperature 25 ° C.) for the test. The temperature was measured by the same method as described above. Example 5
Compared with, the measured temperature was higher and breakthrough could be detected more easily.
実施例6においては、活性炭を下から650mm、その上にF
eOを50mm、更にその上に活性炭を100mm、計800mmの厚さ
となるように充填したものを用いた。それにCl2/N2混合
ガスを毎分10l(室温25℃)で下部より流して試験を行
なった。温度測定は前述と同様な方法で行なった。In Example 6, activated carbon was 650 mm from the bottom and F was placed on top of it.
eO was filled in 50 mm, and activated carbon was further filled in 100 mm so as to have a total thickness of 800 mm. A Cl 2 / N 2 mixed gas was flown from the bottom at 10 l / min (room temperature 25 ° C.) for the test. The temperature was measured by the same method as described above.
実施例8においては、MgOを下から650mm、その上にMg(O
H)2を50mm、更にその上にMgOを100mm、計800mmの厚さと
なるように充填したものを用いた。それにHCl/N2混合ガ
スを毎分10l(室温25℃)で下部より流して試験を行な
った。温度測定は前述と同様な方法で行なった。In Example 8, MgO was 650 mm from the bottom, and Mg (O
H) 2 was filled to 50 mm, and MgO was further filled to 100 mm to a total thickness of 800 mm. A test was conducted by flowing an HCl / N 2 mixed gas at a rate of 10 l / min (room temperature 25 ° C.) from the bottom. The temperature was measured by the same method as described above.
その結果、表−1の検知温度により、破過を確実に検知
することができ、有害ガスが透過することもなく、又、
充填層も飽和間近まで使用することができた。As a result, the breakthrough can be reliably detected by the detection temperatures shown in Table-1, no harmful gas is transmitted, and
The packed bed could also be used up to near saturation.
[異常発熱検知の実施例] 異常発熱の原因に主に、空気中の水分に起因すると考え
られる。そこで、実施例13,14においては、窒素中にF2
を0.5%含む混合ガス、窒素中にBCl3を2%含む混合ガ
スをそれぞれ毎分10l(室温25℃)で100時間流して、破
過の近くまで処理ガスと反応させた後に、絶対湿度1.5
%の空気を毎分500lで吸入させ、充填層高さ680mmの位
置の充填層内の温度を測定した。温度測定はクロメルア
ルメル熱電対をステンレス保護管に入れたものを用い
た。その結果、異常発熱検知温度は、破過検知温度より
も、はるかに高温で容易に破過と異常発熱の区別ができ
た。 [Example of Abnormal Heat Generation Detection] It is considered that the cause of the abnormal heat generation is mainly due to the water content in the air. Therefore, in Examples 13 and 14, F 2 was added in nitrogen.
A mixed gas containing 0.5% of BCl 3 and a mixed gas containing 2% of BCl 3 in nitrogen at 10 l / min (room temperature 25 ° C.) for 100 hours respectively, and reacted with the treated gas up to near breakthrough, and then the absolute humidity 1.5
% Air was inhaled at a rate of 500 l / min, and the temperature inside the packed bed at a height of 680 mm was measured. For temperature measurement, a chromel alumel thermocouple placed in a stainless protective tube was used. As a result, the abnormal heat generation detection temperature was much higher than the breakthrough detection temperature, and it was possible to easily distinguish between the breakthrough and the abnormal heat generation.
[発明の効果] 本発明になる反応熱による破過及び異常発熱の検知方法
は、誤動作が少なく極めて敏感に破過、異常発熱を検知
でき、更に、検知警報及び危険回避処理が自動化できる
優れた長所があり、安全性、運転操作性から排ガスの除
害に効果あるものである。 [Effects of the Invention] The method for detecting breakthrough and abnormal heat generation due to reaction heat according to the present invention is excellent in that it is possible to detect breakthrough and abnormal heat generation extremely sensitively with few malfunctions and further automate detection alarms and risk avoidance processing. It has advantages and is effective in removing exhaust gas from safety and driving operability.
第1図は本発明で用いるエッチング排ガス除害装置を示
す断面図。 3……充填層 7……熱検出器FIG. 1 is a sectional view showing an etching exhaust gas abatement apparatus used in the present invention. 3 ... Packed bed 7 ... Heat detector
───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 昭51−35675(JP,A) 特開 昭54−95968(JP,A) ─────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-51-35675 (JP, A) JP-A-54-95968 (JP, A)
Claims (4)
してこれらを定着することのできる化学反応剤を含む充
填層に、ハロゲンまたはハロゲン化合物を含むエッチン
グ排ガスを導入して除害する方法であって、エッチング
排ガス出口近傍に熱検出器を設け、エッチング排ガスと
化学反応剤の反応熱による温度上昇、および、充填層に
導入される水分と化学反応剤との反応による異常発熱に
よる温度上昇を測定し、異常発熱による温度上昇が反応
熱による温度上昇より高いことを利用して、異常発熱と
充填層の破過とを区別して検知するエッチング排ガス除
害方法。1. A method for removing harm by introducing an etching exhaust gas containing a halogen or a halogen compound into a filling layer containing a chemical reactant capable of chemically reacting with a halogen or a halogen compound to fix them. A heat detector is provided near the etching exhaust gas outlet to measure the temperature rise due to the reaction heat of the etching exhaust gas and the chemical reactant, and the temperature rise due to abnormal heat generation due to the reaction between the water introduced into the packed bed and the chemical reactant, An etching exhaust gas abatement method that distinguishes between abnormal heat generation and breakthrough of a packed bed by utilizing the fact that the temperature rise due to abnormal heat generation is higher than the temperature rise due to reaction heat.
物、アルカリ土類金属の水酸化物、アルカリ土類金属の
炭酸塩、アルカリ金属の炭酸塩、鉄族元素の酸化物、ク
ロム族元素の酸化物からなる群より選ばれる特許請求の
範囲第1項記載のエッチング排ガス除害方法。2. The chemical reaction agent is an alkaline earth metal oxide, an alkaline earth metal hydroxide, an alkaline earth metal carbonate, an alkali metal carbonate, an iron group element oxide, or a chromium group. The method for removing etching exhaust gas according to claim 1, which is selected from the group consisting of oxides of elements.
口近傍に設けた特許請求の範囲第1項記載のエッチング
排ガス除害方法。3. The method for removing etching exhaust gas according to claim 1, wherein a heat detector is provided near the etching exhaust gas outlet in the packed bed.
近傍の充填容器内壁あるいは外壁に設けた特許請求の範
囲第1項記載のエッチング排ガス除害方法。4. The method for removing etching exhaust gas according to claim 1, wherein the heat detector is provided on the inner wall or the outer wall of the filling container near the outlet of the etching exhaust gas of the filling layer.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61282094A JPH0741145B2 (en) | 1986-11-28 | 1986-11-28 | Etching exhaust gas removal method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61282094A JPH0741145B2 (en) | 1986-11-28 | 1986-11-28 | Etching exhaust gas removal method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS63137736A JPS63137736A (en) | 1988-06-09 |
| JPH0741145B2 true JPH0741145B2 (en) | 1995-05-10 |
Family
ID=17648042
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP61282094A Expired - Fee Related JPH0741145B2 (en) | 1986-11-28 | 1986-11-28 | Etching exhaust gas removal method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0741145B2 (en) |
Families Citing this family (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH03181316A (en) * | 1989-12-12 | 1991-08-07 | Ebara Res Co Ltd | Method for making nf3 harmless |
| JPH06177B2 (en) * | 1990-02-05 | 1994-01-05 | 株式会社荏原総合研究所 | Method for treating exhaust gas containing C1F (bottom 3) |
| JP2574816Y2 (en) * | 1990-07-09 | 1998-06-18 | 三菱電機株式会社 | Exhaust gas abatement system |
| JPH0716583B2 (en) * | 1990-08-10 | 1995-03-01 | セントラル硝子株式会社 | Method for dry treatment of exhaust gas containing chlorine fluoride |
| JPH04156919A (en) * | 1990-10-19 | 1992-05-29 | Ebara Res Co Ltd | Treatment of exhaust gas containing halogen compound |
| JPH062213B2 (en) * | 1990-10-23 | 1994-01-12 | 岩谷産業株式会社 | Halogen-based waste gas dry treatment agent |
| JPH06198128A (en) * | 1993-12-01 | 1994-07-19 | Ebara Res Co Ltd | Treatment of waste gas containing halogen compound |
| KR20090019791A (en) * | 2006-05-19 | 2009-02-25 | 아사히 가라스 가부시키가이샤 | Removal method of halogen gas and removal agent of halogen gas |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5135675A (en) * | 1974-09-20 | 1976-03-26 | Hitachi Ltd | KYUCHAKU SOCHI |
| JPS5495968A (en) * | 1978-01-13 | 1979-07-28 | Toshiba Corp | Deodorizing apparatus using ozone |
| JPS60125233A (en) * | 1983-12-08 | 1985-07-04 | Mitsui Toatsu Chem Inc | High degree treatment of exhaust gas |
| JPS6153555A (en) * | 1984-08-23 | 1986-03-17 | Ube Ind Ltd | How to predict breakthrough in gas adsorption equipment |
-
1986
- 1986-11-28 JP JP61282094A patent/JPH0741145B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPS63137736A (en) | 1988-06-09 |
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