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JP3776576B2 - Semiconductor manufacturing exhaust gas abatement apparatus and abatement method - Google Patents
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JP3776576B2 - Semiconductor manufacturing exhaust gas abatement apparatus and abatement method - Google Patents

Semiconductor manufacturing exhaust gas abatement apparatus and abatement method Download PDF

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Publication number
JP3776576B2
JP3776576B2 JP32250397A JP32250397A JP3776576B2 JP 3776576 B2 JP3776576 B2 JP 3776576B2 JP 32250397 A JP32250397 A JP 32250397A JP 32250397 A JP32250397 A JP 32250397A JP 3776576 B2 JP3776576 B2 JP 3776576B2
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Prior art keywords
cylinder
exhaust gas
decomposition
abatement
disassembly
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JPH11137951A (en
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啓志 今村
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Kanken Techno Co Ltd
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Kanken Techno Co Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は半導体,液晶等の製造に伴い発生する排ガスの除害装置及び除害方法に関するものである。
【0002】
【従来の技術】
半導体製造において発生する排ガスの除害方法には乾式(吸着)、燃焼式(燃料使用による火炎分解)、加熱酸化分解方式(電熱方式)、湿式(水又は薬液使用による吸収溶解,乃至分解)があり、一長一短の特徴や問題点を有するが、装置の安全性,除害性,コンパクト性,制御性,コスト面から見て加熱酸化分解方式の優位性が評価されている。
【0003】
しかしながら、加熱酸化分解方式においては例えばSiH4に対してはSiO2、PH3に対してはP25のように、処理後には排ガスの酸化物としての粉塵が分解筒内部に副生し、ガス通路の各所に滞積して通気抵抗が高くなっていく。
【0004】
それ故、通常は除害装置の稼働時間を決め、所定時間稼働した後に一旦除害装置のヒータ通電を停止し、分解筒内を降温せしめ(例えば100℃以下にしてから)上部より水シャワーをかけてヒータ表面を含む各所に滞積した粉塵を洗い落とすか、あるいは分解筒を解体して内部を手動で洗浄していた。いずれにしても除害機はその間停止するので、それに接続されたCVDによる半導体生産はストップし、生産性の低下は明らかであった。
【0005】
【発明が解決しようとする課題】
本発明はこのような問題点を解決し、半導体製造工程においてCVDの操業に影響を与えることなく排ガスの除害を安全に継続して行うことを可能とし、継続操業により半導体の生産性を高める手段が求められている。
【0006】
【課題を解決するための手段】
本発明の半導体排ガスの除害装置は、排ガスの導入部と処理後の放出部に夫々水スクラバを有し、その導入部水スクラバと放出部水スクラバとの間に2個又は3個の電熱式酸化加熱の分解筒が備えられており、排ガス処理のために稼働する分解筒を切り換え可能であることを特徴とする。
【0007】
又、本発明の半導体排ガスの除害方法は、請求項1記載の半導体排ガスの除害装置を用い、稼働中の分解筒に副生粉塵が滞積してガスの通過抵抗が所定値以上となった際、又は分解筒を所定時間稼働させた後に、稼働中の分解筒を待機中の分解筒に切り換え、稼働を停止した分解筒は副生粉塵を除去して次回の分解筒切換のために待機させることにより、継続して排ガスの除害が行えるようにすることを特徴とする。
【0008】
本発明の除害装置は特開平7-323211号に記載の除害装置のように、処理ガスの流れに沿って入口側と出口側に夫々水スクラバを設け、その中央に電熱式酸化加熱分解筒を備えている。更に、本発明では分解筒を2個乃至3個設け、排ガス処理と副生粉塵除去とを夫々別個の分解筒において同時並行的に行い、それを所定時間毎に順次切換する。
【0009】
すなわち、副生粉塵除去を行う分解筒に対しては排ガスの導入を遮断し、通電を停止の上、室温にまで降温した後に加圧空気又はN2ガスのスプレー,水のスプレーのいずれかによる粉塵除去し,必要なら分解筒の内部解体による全面的清掃を行う。内部が充分乾燥した後、次の除害用分解筒として待機させる。除害機のこのような使用方法によりCVDの操業停止すること排ガスを除害することができる。
【0010】
CVDでデポジットとクリーニングとを反復せしめる工程において、両者のガス、例えばSiH4とNF3の如き相互に混合することにより爆発の危険性がある場合には、例えば分解筒の3連方式とすることが効果的である。
【0011】
その場合、各分解筒をA,B,Cとすると、分解筒Aをデポジット用,分解筒Bをクリーニング用の排ガス処理させれば、分解筒Cはデポジット用の清掃待機筒とすることができる。CVDの操業に合わせて分解筒Aと分解筒Bとに適宜排ガスをバルブ切り換えによって導入させて別個に除害を行う。
【0012】
粉塵発生はデポジット用排ガスを処理する分解筒Aのみに生じるので、分解筒Cは分解筒A用の待機筒となる。Bは通常は清掃作業の必要はない。このように分解筒Aと分解筒Cを交互に用いてデポジット用排ガスの除害と清掃作業を行うことによりCVDの操業停止することなく排ガスを除害することができる。
【0013】
【発明の実施の形態】
以下、本発明を好適な実施例を用いて説明する。
[実施例]
図1は本発明の除害装置の概念図である。キャビネット(1)内に同一寸法,同一機能の加熱酸化分解筒A(A)及びB(B)が収納されている。排ガスは図の左側から入り、処理されたガスが右側から放出される。分解筒A及びBの処理量は1000リットル/minとした。(2)は夫々の分解筒の水洗浄用の水スプレー部である。
【0014】
図2はこの除害装置の運転のタイミングを説明する図である。分解筒A,Bは交互に休止状態となり、洗浄水は分解筒A,Bが休止状態にあるときに噴射される。同図中Wは除害作業を示し、Mはメンテナンスすなわち清掃作業を示す。ヒータ温度は除害作業時は700℃、メンテナンス時は100℃となるようにしている。切換に際しては待機している分解筒のヒータ温度を700℃に昇温させてから切換を行っているので、除害作業はスムーズに切り換えられる。
【0015】
[実施例1]
LPーCVD(低圧CVD)の使用においてSiH4が1.2リットル/min(ガス濃度は100%濃度。以下ことわりない限り同様)、NH3が1リットル/min、PH3(N2バランスで0.5%)1.2リットル/min、H2が1リットル/min 、N2が308リットル/minの混合ガスを供給し、それからの排気ガスを除害機に排出させた。
【0016】
この排ガスを供給水10リットル/minの水量によるスプレー部を通過させ、13.5kWの電気容量を持ったヒーターを具備した酸化加熱分解筒に導入した。ここには排ガス導入管とは別系統で外部空気をポンプで52リットル/min供給し、分解筒内で混合して酸化除害せしめた。分解後のガスは出口で入口と同じ条件での10リットル/min供給水でシャワー洗浄した後に外部に放出した。電熱ヒータの表面温度は700℃に設定した。
【0017】
また、キャビネット内には、この分解筒と同じ形状,能力を有する別個の分解筒を設置している。
【0018】
かかる状況下において1週間の継続使用を続けたところ、除害に用いている分解筒内部の通気抵抗の状況を表示する静圧計にて初期圧0.5kPaであったのが、1kPaに達した。
【0019】
排ガス導入経路の内部を清掃し、ヒータの温度を700℃に保った待機用の分解筒に切り換え、CVDの操業は何ら変更しないまま除害装置を稼働せしめた。
【0020】
それまで除害に使用していた分解筒は通電停止して室温にまで降温させ、その後分解筒の上部に設置してある水スプレーノズルより水を噴射せしめて内部に滞積した粉塵を洗い落とした。覗き窓より見て白色の粉塵の滞積がなくなったことを確認後、加圧空気を通して乾燥させ、標準状態のガス流速下静圧測定した結果0.5kPaとなっていることを確認した。
【0021】
このようにして洗浄された分解筒は、待機筒として次回の切換に備える。1週間後、上記と同じ操作にて分解筒の切り替えを行った。これらの作業中CVDは停止せず、生産性は全く低下させることはなかった。尚、大気放出ガス中のSiH4は1ppm以下、PH3は全く検出されなかった。
【0022】
[実施例2]
本実施例では実施例1と同じ構成の除害機に3連の分解筒A,B,Cを設置した装置を使用した。
【0023】
PーCVD(プラズマCVD)においてTEOS(テトラエトキシシラン)が1リットル/min、NH3が4リットル/min、H2が5リットル/min、N2が95リットル/minのデポジットガスを使用し、更にクリーニングプロセスにおいてNF3が4リットル/min、Arが0.5リットル/min、N2が80リットル/minの混合ガスを使用した。
【0024】
分解筒Aにはデポジット排ガスを、分解筒Bにはクリーニング排ガスを導入した。尚、分解筒A及びBのヒータ表面温度を800℃に設定した。分解筒A,Bへのガス導入経路切り換えはCVD出口におけるバルブの自動制御によった。
【0025】
分解筒AにはSiO2粉塵が滞積したが、分解筒Bには何ら粉塵の痕跡は認められなかった。NH3はほとんどが入口側の水スクラバにおいて水中に溶存除去された。
【0026】
実施例1の場合と同様に1週間の継続運転の後、分解筒Aから待機している分解筒Cに切り換え、分解筒Bはそのままで使用を継続した。その切り換えの過程でCVDの生産性には何ら影響を与えずに操業を継続することができた。尚、放出ガス中のTEOSは1ppm以下、NF3は0.5ppm以下であった。
【0027】
【発明の効果】
以上述べたように本発明により、半導体製造工程においてCVDの操業に影響を与えることなく排ガスの除害を継続して行うことが可能となり、継続操業による半導体の生産性を高めることができた。
【図面の簡単な説明】
【図1】本発明の除害装置の概念図。
【図2】除害装置の運転のタイミングを説明する図。
【符号の説明】
(1) キャビネット
(2) 水スプレー部
(A) 加熱酸化分解筒
(B) 加熱酸化分解筒
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to an apparatus and method for removing exhaust gas generated in the manufacture of semiconductors, liquid crystals and the like.
[0002]
[Prior art]
Methods for removing exhaust gas generated in semiconductor manufacturing include dry (adsorption), combustion (flame decomposition using fuel), thermal oxidative decomposition (electric heating method), and wet (absorption dissolution or decomposition using water or chemicals). However, it has advantages and disadvantages, but the superiority of the thermal oxidative decomposition method is evaluated from the viewpoint of safety, abatement, compactness, controllability, and cost of the device.
[0003]
However, in the heat oxidative decomposition method, for example, SiO 2 for SiH 4 and P 2 O 5 for PH 3 , dust as exhaust gas oxide is by-produced inside the decomposition cylinder after treatment. The gas flow resistance increases as it accumulates in various parts of the gas passage.
[0004]
Therefore, normally, the operating time of the abatement device is determined, and after the specified time has elapsed, the heater energization of the abatement device is stopped once, and the temperature inside the decomposition cylinder is lowered (for example, after 100 ° C. or less), a water shower is provided from the top The dust accumulated in various places including the heater surface was washed off, or the disassembly cylinder was disassembled and the inside was manually cleaned. In any case, since the abatement machine stops during that time, the semiconductor production by CVD connected thereto is stopped, and the reduction in productivity is obvious.
[0005]
[Problems to be solved by the invention]
The present invention solves such problems and makes it possible to safely and continuously perform exhaust gas elimination without affecting the CVD operation in the semiconductor manufacturing process, and increase the productivity of the semiconductor by the continuous operation. Means are sought.
[0006]
[Means for Solving the Problems]
The semiconductor exhaust gas abatement apparatus of the present invention has water scrubbers at the exhaust gas introduction part and the treated discharge part, respectively, and two or three electric heats between the introduction part water scrubber and the discharge part water scrubber. A decomposition cylinder of the type oxidation heating is provided, and the decomposition cylinder operating for exhaust gas treatment can be switched.
[0007]
The semiconductor exhaust gas abatement method of the present invention uses the semiconductor exhaust gas abatement apparatus according to claim 1, and by-product dust accumulates in the operating decomposition cylinder, and the gas passage resistance is a predetermined value or more. Or after operating the decomposition cylinder for a predetermined time, switch the active decomposition cylinder to the standby decomposition cylinder. It is characterized in that exhaust gas can be removed continuously by making it stand by.
[0008]
The abatement apparatus of the present invention is provided with water scrubbers on the inlet side and the outlet side along the flow of the processing gas, respectively, as in the abatement apparatus described in JP-A-7-323211, and electrothermal oxidation pyrolysis at the center. It has a cylinder. Further, in the present invention, two to three decomposition cylinders are provided, exhaust gas treatment and by-product dust removal are simultaneously performed in separate decomposition cylinders, and they are sequentially switched every predetermined time.
[0009]
That is, for the decomposition cylinder that removes by-product dust, cut off the introduction of exhaust gas, stop energization, cool to room temperature, and then use either pressurized air, N 2 gas spray, or water spray Remove dust, and if necessary, clean the entire disassembly cylinder by dismantling. After the interior is sufficiently dried, it is put on standby as the next decomposing cylinder for detoxification. By stopping the CVD operation, exhaust gas can be removed by such a method of using the remover.
[0010]
In the process of repeating deposition and cleaning by CVD, if there is a risk of explosion by mixing both gases, such as SiH 4 and NF 3 , for example, a triple decomposition system is used. Is effective.
[0011]
In this case, if each decomposition cylinder is A, B, and C, the decomposition cylinder C can be used as a deposit cleaning standby cylinder if the decomposition cylinder A is treated for depositing and the decomposition cylinder B is treated for cleaning. . In accordance with the operation of the CVD, exhaust gas is appropriately introduced into the decomposition cylinder A and the decomposition cylinder B by switching the valves, and the detoxification is performed separately.
[0012]
Since dust generation occurs only in the decomposition cylinder A that processes the exhaust gas for deposit, the decomposition cylinder C becomes a standby cylinder for the decomposition cylinder A. B usually does not need to be cleaned. In this way, by using the decomposition cylinder A and the decomposition cylinder C alternately to perform detoxification and cleaning of the exhaust gas for deposit, the exhaust gas can be detoxified without stopping the CVD operation.
[0013]
DETAILED DESCRIPTION OF THE INVENTION
The present invention will be described below with reference to preferred embodiments.
[Example]
FIG. 1 is a conceptual diagram of the abatement apparatus of the present invention. The heating oxidation decomposition cylinders A (A) and B (B) having the same dimensions and the same functions are accommodated in the cabinet (1). The exhaust gas enters from the left side of the figure, and the treated gas is released from the right side. The throughput of the decomposition cylinders A and B was 1000 liters / min. (2) is a water spray section for water cleaning of each disassembly cylinder.
[0014]
FIG. 2 is a diagram for explaining the operation timing of the abatement apparatus. The decomposition cylinders A and B are alternately in a resting state, and the cleaning water is injected when the decomposition cylinders A and B are in a resting state. In the figure, W indicates a detoxification operation, and M indicates maintenance, that is, a cleaning operation. The heater temperature is set to 700 ° C. during detoxification work and 100 ° C. during maintenance. At the time of switching, since the switching is performed after raising the heater temperature of the stand-by disassembly cylinder to 700 ° C., the detoxification work can be switched smoothly.
[0015]
[Example 1]
When using LP-CVD (low pressure CVD), SiH 4 is 1.2 liters / min (gas concentration is 100%, unless otherwise noted), NH 3 is 1 liter / min, PH 3 (N 2 balance is 0.5%) A mixed gas of 1.2 liter / min, H 2 of 1 liter / min, and N 2 of 308 liter / min was supplied, and the exhaust gas from the mixed gas was discharged to a detoxifier.
[0016]
This exhaust gas was passed through a spray section with a water amount of 10 liters / min of supply water, and introduced into an oxidation pyrolysis cylinder equipped with a heater having an electric capacity of 13.5 kW. Here, external air was supplied at a rate of 52 liters / min by a pump in a separate system from the exhaust gas introduction pipe, and was mixed in the decomposition cylinder for oxidative detoxification. The decomposed gas was discharged to the outside after shower-washing with 10 liter / min feed water at the outlet under the same conditions as the inlet. The surface temperature of the electric heater was set to 700 ° C.
[0017]
In the cabinet, a separate disassembly cylinder having the same shape and capacity as this disassembly cylinder is installed.
[0018]
Under such circumstances, when the continuous use was continued for one week, the initial pressure of 0.5 kPa reached 1 kPa in the static pressure gauge displaying the state of the ventilation resistance inside the disassembly cylinder used for the detoxification. .
[0019]
The inside of the exhaust gas introduction path was cleaned and switched to a stand-by decomposition cylinder in which the heater temperature was kept at 700 ° C., and the abatement apparatus was operated without any change in the CVD operation.
[0020]
The disassembly cylinder that had been used for detoxification was de-energized and cooled to room temperature, and then water was sprayed from the water spray nozzle installed at the top of the disassembly cylinder to wash away the dust accumulated inside. . After confirming that there was no accumulation of white dust as seen from the viewing window, it was dried through pressurized air, and it was confirmed that it was 0.5 kPa as a result of static pressure measurement under standard gas flow rate.
[0021]
The disassembled cylinder cleaned in this way is prepared for the next switching as a standby cylinder. One week later, the disassembly cylinder was switched by the same operation as described above. During these operations, CVD did not stop and productivity was not reduced at all. In addition, SiH 4 in the atmospheric emission gas was 1 ppm or less, and PH 3 was not detected at all.
[0022]
[Example 2]
In the present embodiment, an apparatus in which three disassembly cylinders A, B, and C are installed in the abatement apparatus having the same configuration as that of the first embodiment is used.
[0023]
In P-CVD (plasma CVD), TEOS (tetraethoxysilane) is 1 liter / min, NH 3 is 4 liter / min, H 2 is 5 liter / min, and N 2 is 95 liter / min. Further, in the cleaning process, a mixed gas having NF 3 of 4 liter / min, Ar of 0.5 liter / min, and N 2 of 80 liter / min was used.
[0024]
Deposited exhaust gas was introduced into the decomposition cylinder A, and cleaning exhaust gas was introduced into the decomposition cylinder B. The heater surface temperature of the decomposition cylinders A and B was set to 800 ° C. Switching of the gas introduction path to the decomposition cylinders A and B was performed by automatic control of a valve at the CVD outlet.
[0025]
Although SiO 2 dust stagnated in the decomposition cylinder A, no trace of dust was observed in the decomposition cylinder B. Most of NH 3 was dissolved and removed in water in the water scrubber on the inlet side.
[0026]
As in the case of Example 1, after one week of continuous operation, the disassembly cylinder A was switched to the stand-by disassembly cylinder C, and the disassembly cylinder B was used as it was. In the process of switching, the operation could be continued without affecting the productivity of CVD. Note that TEOS in the released gas was 1 ppm or less, and NF 3 was 0.5 ppm or less.
[0027]
【The invention's effect】
As described above, according to the present invention, exhaust gas removal can be continuously performed without affecting the CVD operation in the semiconductor manufacturing process, and the productivity of the semiconductor by the continuous operation can be improved.
[Brief description of the drawings]
FIG. 1 is a conceptual diagram of an abatement apparatus of the present invention.
FIG. 2 is a diagram for explaining the operation timing of the abatement apparatus.
[Explanation of symbols]
(1) Cabinet
(2) Water spray section
(A) Heat oxidation cracking cylinder
(B) Heat oxidation decomposition cylinder

Claims (2)

排ガスの導入部と処理後の放出部に夫々水スクラバを有し、その導入部水スクラバと放出部水スクラバとの間に2個又は3個の電熱式酸化加熱の分解筒が備えられており、排ガス処理のために稼働する分解筒を切り換え可能である
ことを特徴とする半導体製造排ガスの除害装置。
Each of the exhaust gas introduction part and the treated discharge part has a water scrubber, and two or three electrothermal oxidation heating decomposition cylinders are provided between the introduction part water scrubber and the discharge part water scrubber. A semiconductor manufacturing exhaust gas abatement apparatus characterized in that a disassembly cylinder operating for exhaust gas treatment can be switched.
請求項1記載の半導体製造排ガスの除害装置を用い、
稼働中の分解筒に副生粉塵が滞積してガスの通過抵抗が所定値以上となった際、又は分解筒を所定時間稼働させた後に、稼働中の分解筒を待機中の分解筒に切り換え、稼働を停止した分解筒は副生粉塵を除去して次回の分解筒切換のために待機させることにより、継続して排ガスの除害が行えるようにする
ことを特徴とする半導体製造排ガスの除害方法。
Using the semiconductor manufacturing exhaust gas abatement apparatus according to claim 1,
When the by-product dust accumulates in the operating decomposition cylinder and the gas passage resistance exceeds a predetermined value, or after the decomposition cylinder has been operated for a predetermined time, the operating decomposition cylinder is changed to a standby decomposition cylinder. The disassembly cylinder that has been switched off and stopped is used to remove the by-product dust and wait for the next disassembly cylinder switchover so that the exhaust gas can be removed continuously. Detoxification method.
JP32250397A 1997-11-07 1997-11-07 Semiconductor manufacturing exhaust gas abatement apparatus and abatement method Expired - Lifetime JP3776576B2 (en)

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JP32250397A JP3776576B2 (en) 1997-11-07 1997-11-07 Semiconductor manufacturing exhaust gas abatement apparatus and abatement method

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