JP3490751B2 - Decomposition method of gaseous fluoride - Google Patents
Decomposition method of gaseous fluorideInfo
- Publication number
- JP3490751B2 JP3490751B2 JP28110593A JP28110593A JP3490751B2 JP 3490751 B2 JP3490751 B2 JP 3490751B2 JP 28110593 A JP28110593 A JP 28110593A JP 28110593 A JP28110593 A JP 28110593A JP 3490751 B2 JP3490751 B2 JP 3490751B2
- Authority
- JP
- Japan
- Prior art keywords
- fluoride
- gaseous
- hydrogen fluoride
- decomposition
- gas
- 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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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、半導体エッチングプロ
セスから排気されるガス、或いはその補修時に空調設備
等から排出される冷媒の気体状フッ化物又は気体状フッ
化物を含有する気体を分解する方法、さらには分解によ
り生成した気体を吸着剤で処理して無害化する方法に関
するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for decomposing a gas exhausted from a semiconductor etching process, or a gaseous fluoride or a gas containing the gaseous fluoride of a refrigerant exhausted from an air conditioner or the like when repairing the gas. Furthermore, the present invention relates to a method of detoxifying the gas produced by decomposition by treating it with an adsorbent.
【0002】[0002]
【従来の技術】半導体のエッチングプロセスで使用され
ている気体状フッ化物、例えばCF4、C2 F6 、C3
F8 、CHF3 、CH2 F2 、SF6 、NF3 等は、当
該プロセスで使用するために印加しても、10〜30%
程度が分解してエッチングに使用されるだけで、残りの
70〜90%は使用されることなく排出され、大気中に
放出されてしまう。また冷凍設備、冷蔵庫或いは空調装
置で使用されているクロロフルオロカーボン(CFC)
−11、12の様な気体も補修時にはその総てを捕捉す
ることはできず、一部は大気中へ放出されてしまう。Gaseous fluorides used in semiconductor etching processes, such as CF 4 , C 2 F 6 , C 3
F 8, CHF 3, CH 2 F 2, SF 6, NF 3 or the like, be applied for use in the process, 10-30%
Only to a certain extent, it is decomposed and used for etching, and the remaining 70 to 90% is exhausted without being used and released into the atmosphere. Chlorofluorocarbon (CFC) used in refrigeration equipment, refrigerators or air conditioners
All of the gases such as -11 and 12 cannot be captured during repair, and some of them are released into the atmosphere.
【0003】しかし、これらの気体は地球温暖化に寄与
するガスと言われており、またCFCは周知の様にオゾ
ン層を破壊する物質として、その生産と消費のフェーズ
アウトスケジュールが決められている物質である。さら
にNF3 は大気中に放出するにはその有害性が問題とな
る。従って、これらの気体は大気中に放出する前に分解
して環境への影響を無くする必要がある。However, these gases are said to contribute to global warming, and as is well known, CFC is a substance that destroys the ozone layer, and the phase-out schedule for its production and consumption is determined. It is a substance. Furthermore, the harmfulness of NF 3 becomes a problem when it is released into the atmosphere. Therefore, it is necessary to decompose these gases before releasing them into the atmosphere to eliminate the influence on the environment.
【0004】このため、燃焼法、プラズマ分解法、酸化
分解法、水素化分解法、超臨界水法、微生物分解法等
々、これらの気体状フッ化物を分解する方法が種々検討
・提案されている。しかしながら、これらの内で実際に
商業規模で実施されているのは燃焼法のみであり、その
他は未だ試験段階にあると言うのが実情である。Therefore, various methods for decomposing these gaseous fluorides such as a combustion method, a plasma decomposition method, an oxidative decomposition method, a hydrogenolysis method, a supercritical water method, and a microbial decomposition method have been studied and proposed. . However, of these, only the combustion method is actually used on a commercial scale, and the others are still in the trial stage.
【0005】燃焼法は排出される気体を、水素/酸素、
プロパン、都市ガス等で燃焼させ、生成したガスをアル
カリ等で洗浄し、フッ素イオンはフッ化カルシウム等の
形で固定化する方法である。In the combustion method, the gas discharged is hydrogen / oxygen,
This is a method of burning with propane, city gas, etc., washing the generated gas with an alkali, etc., and fixing the fluoride ions in the form of calcium fluoride or the like.
【0006】燃焼法により気体状フッ化物、特に半導体
のエッチングプロセスで使用されるエッチングガス又は
クリーニングガスを処理する場合、
1)安定なガスであるため、直接火炎中に混入する必要
があり、炎の状態が不安定になり、消炎状態を惹起し、
未燃焼ガスが炉の内部にたまり、爆発を起こす危険があ
る。
2)多量の空気を必要とするため、クリーンルーム内の
空気制御に影響を及ぼす。
3)多量の空気が排ガス中に混入するため、燃焼後の排
ガス処理装置を大型化する必要があり、設備費及び処理
経費が増加する。
4)フッ化物がバーナーの腐食の原因になる。
5)燃焼時の騒音が問題になる。
等々の欠点がある。When a gaseous fluoride, particularly an etching gas or a cleaning gas used in a semiconductor etching process, is processed by a combustion method, 1) it is a stable gas, and therefore it is necessary to directly mix it in a flame. Becomes unstable and causes an extinguishing condition,
Unburned gas may accumulate inside the furnace and cause an explosion. 2) A large amount of air is required, which affects air control in the clean room. 3) Since a large amount of air is mixed in the exhaust gas, it is necessary to upsize the exhaust gas processing device after combustion, which increases equipment costs and processing costs. 4) Fluoride causes burner corrosion. 5) Noise during combustion becomes a problem. There are drawbacks, etc.
【0007】[0007]
【発明が解決しようとする課題】そのため、気体状フッ
化物を効率的に分解・無害化して放出できる安価な方法
・装置の開発が望まれているのが現状である。したがっ
て、本発明の目的は、従来から行われている燃焼法の欠
点を解消し、効率的で安価な気体状フッ化物の分解法、
さらには分解生成物を吸着処理することにより大気中に
有害ガスの放出を防止する方法の提供にある。Therefore, at present, there is a demand for the development of an inexpensive method / apparatus capable of efficiently decomposing and detoxifying gaseous fluorides and releasing them. Therefore, the object of the present invention is to eliminate the drawbacks of the conventional combustion method, an efficient and inexpensive decomposition method of gaseous fluoride,
Another object is to provide a method for preventing the release of harmful gas into the atmosphere by subjecting decomposition products to adsorption treatment.
【0008】[0008]
【課題を解決するための手段】本発明は(1)気体状フ
ッ化物(フッ化水素を除く)又は気体状フッ化物を含有
する気体(フッ化水素を除く)をフッ化水素の共存下、
500℃〜1500℃の温度でSi又はBの酸化物の内
から選択された1種以上よりなる分解剤と接触させるこ
とを特徴とする気体状フッ化物(フッ化水素を除く)の
分解方法、及び(2)分解により生成した気体を、活性
アルミナ、ゼオライト、ソーダライム、シリカゲルの内
から選択された1種以上の吸着主剤と亜硫酸ナトリウ
ム、チオ硫酸ナトリウム、酸化マンガン/酸化銅、過マ
ンガン酸カリウムの内から選択された1種以上の吸着補
助剤とからなる吸着剤と接触させる工程をさらに含むこ
とを特徴とする上記分解方法を提供する。Means for Solving the Problems The present invention (1) (except hydrogen fluoride) gaseous fluoride or (except hydrogen fluoride) gas containing gaseous fluoride presence of hydrogen fluoride,
A method for decomposing gaseous fluorides (excluding hydrogen fluoride) , which comprises contacting with a decomposing agent consisting of one or more kinds selected from oxides of Si or B at a temperature of 500 ° C to 1500 ° C , And (2) the gas generated by the decomposition is treated with at least one adsorbent main agent selected from activated alumina, zeolite, soda lime, and silica gel, and sodium sulfite, sodium thiosulfate, manganese oxide / copper oxide, potassium permanganate. The above-mentioned decomposition method is characterized by further comprising a step of contacting with an adsorbent consisting of one or more adsorption aids selected from the above.
【0009】本発明によれば、半導体エッチングプロセ
スから排気されるガス、或いは補修時に空調設備等から
排出される冷媒の気体状フッ化物は気体状フッ化物を含
有する気体等を効率的に分解できる。また、本発明は従
来の燃焼法の欠点を解消し、次の利点がある。
1)炎を使用しないため、火が消えたり不完全燃焼を生
ずることがない。
2)温度の制御が容易である。
3)多量の空気を必要とせず、排ガス全体が少ない。
4)装置全体がコンパクトになる。
すなわち、高価なクリーンルームの床を有効に利用で
き、また空気管理も容易となり、さらには騒音もなくな
るのである。According to the present invention, the gas exhausted from the semiconductor etching process or the gaseous fluoride of the refrigerant exhausted from the air conditioning equipment at the time of repair can efficiently decompose the gas containing the gaseous fluoride. . Further, the present invention solves the drawbacks of the conventional combustion method and has the following advantages. 1) Since no flame is used, there is no possibility of extinguishing the fire or incomplete combustion. 2) It is easy to control the temperature. 3) A large amount of air is not required, and the total amount of exhaust gas is small. 4) The entire device becomes compact. That is, the floor of an expensive clean room can be effectively used, the air management is facilitated, and the noise is eliminated.
【0010】本発明の方法が適用できる気体状フッ化物
としては、半導体のエッチングプロセスで使用されてい
る気体状フッ化物、CF4 、C2 F6 、C3 F8 、CH
F3、CH2 F2 、SF6 、NF3 等及びこれらを含む
エッチングプロセスからの排出ガス、これらを含むエッ
チング装置のクリーニングガス、さらにはCFC類、ハ
イドロクロロフルオロカーボン(HCFC)類、ハイド
ロフルオロカーボン(HFC)類を挙げることができ
る。Gaseous fluorides to which the method of the present invention can be applied include gaseous fluorides used in semiconductor etching processes, such as CF 4 , C 2 F 6 , C 3 F 8 and CH.
F 3, CH 2 F 2, SF 6, NF 3 or the like and the exhaust gas from the etching process including these, cleaning gases, more CFC's of the etching apparatus including these, hydrochlorofluorocarbons (HCFC) such, hydrofluorocarbons ( HFCs) can be mentioned.
【0011】また、本発明に使用する分解剤Si又はB
の酸化物の内では、特にSiの酸化物が好ましく、より
具体的には酸化ケイ素、ハイシリカゼオライトを挙げる
ことができる。The decomposing agent used in the present invention is Si or B.
Of these oxides, Si oxide is particularly preferable, and more specifically, silicon oxide and high silica zeolite can be mentioned.
【0012】吸着剤は、活性アルミナ、ゼオライト、ソ
ーダライム、シリカゲルの内から選択された1種以上の
吸着主剤と亜硫酸ナトリウム、チオ硫酸ナトリウム、酸
化マンガン/酸化銅、過マンガン酸カリウムの内から選
択された1種以上の吸着補助剤とからなり、吸着主剤と
吸着補助剤の比率は容量で1:0.01〜1:0.1、
特に好ましくは1:0.05〜1:0.08であり、混
合して使用する。The adsorbent is selected from one or more adsorbent main agents selected from activated alumina, zeolite, soda lime and silica gel, and sodium sulfite, sodium thiosulfate, manganese oxide / copper oxide and potassium permanganate. One or more of the adsorbent adsorbents, and the ratio of the adsorbent main agent to the adsorbent adjunct is 1: 0.01 to 1: 0.1 by volume,
It is particularly preferably 1: 0.05 to 1: 0.08, and the mixture is used.
【0013】フッ化水素は最も反応性の強いハロゲン化
水素であり、分解剤と極めてよく反応する。例えば分解
剤の表面での
SiO2 +4HF → SiF4 +2H2 O
の反応により、SiF4 及びH2 Oが揮発し、分解剤の
表面がポーラスになり、より効率良く気体状フッ化物と
反応するようになる。Hydrogen fluoride is the most reactive hydrogen halide and reacts extremely well with decomposers. For example, due to the reaction of SiO 2 + 4HF → SiF 4 + 2H 2 O on the surface of the decomposing agent, SiF 4 and H 2 O are volatilized, the surface of the decomposing agent becomes porous, and more efficiently reacts with the gaseous fluoride. become.
【0014】フッ化水素の量は気体状フッ化物の量に対
して容量換算で1%以上であることが好ましく、1%未
満では本発明の効果が得られず、分解率が低下する。ま
た、上限は特に無いが、フッ化水素の量が多いと吸着剤
に対する負荷が大きくなり、吸着剤の寿命が短くなる。
従って実用的範囲は10%以下となる。また、分解温度
は500℃以上であれば充分な分解率が得られる。しか
し、500℃未満でも気体状フッ化物の仕込み速度を遅
くすれば分解率を維持することができる。但し、あまり
仕込み速度が遅くなると実用的でなくなるので500℃
以上とした。一方温度の上限は特にないが炉の耐熱温度
等を考慮すると1500℃以上では実用的でない。よっ
て、500〜1500℃が好ましい。 The amount of hydrogen fluoride is preferably 1% or more in terms of volume with respect to the amount of gaseous fluoride, and if it is less than 1%, the effect of the present invention cannot be obtained and the decomposition rate decreases. Further, although there is no particular upper limit, if the amount of hydrogen fluoride is large, the load on the adsorbent becomes large and the life of the adsorbent becomes short.
Therefore, the practical range is 10% or less. Further, if the decomposition temperature is 500 ° C. or higher, a sufficient decomposition rate can be obtained. However, even if the temperature is lower than 500 ° C., the decomposition rate can be maintained by slowing the charging rate of the gaseous fluoride. However, if the charging speed becomes too slow, it will not be practical, so 500 ° C
That's it. On the other hand, there is no particular upper limit to the temperature, but considering the heat-resistant temperature of the furnace and the like, it is not practical at 1500 ° C or higher. Yo
Therefore, the temperature is preferably 500 to 1500 ° C.
【0015】以下に、第1図により本発明の実施に使用
する装置の一例の概略ブロック図を示す。1は気体状フ
ッ化物を仕込むラインである。2はフッ化水素の導入管
である。3は分解剤の導入管で、連続的に分解処理をす
る場合にこのラインを通して分解剤を系内に入れる。5
は分解剤が充填されている分解器であり、6の電気加熱
器により加熱される。7は温度制御装置で、これにより
分解器の温度を制御する。FIG. 1 shows a schematic block diagram of an example of an apparatus used for implementing the present invention. 1 is a line for charging gaseous fluoride. Reference numeral 2 is a hydrogen fluoride introduction tube. Reference numeral 3 is a decomposing agent introducing pipe, and when decomposing continuously, the decomposing agent is introduced into the system through this line. 5
Is a decomposer filled with a decomposer, and is heated by an electric heater 6; A temperature controller 7 controls the temperature of the decomposer.
【0016】4は場合によりフッ化水素導入管として使
用するか、或いは系内の窒素置換等に使用する予備的な
ものである。8は冷却器であり、分解後のガスを常温近
くまで冷却する。本例では冷却媒体として水を使用して
いる。9、11はサンプリングポートを示し、10は吸
着剤が充填されている吸着筒で、分解後のガスを無害化
し、12の放出パイプより無害化されたガスが放出され
る。Numeral 4 is a preliminary one which is used as a hydrogen fluoride introduction pipe in some cases or used for nitrogen substitution in the system. A cooler 8 cools the decomposed gas to near room temperature. In this example, water is used as the cooling medium. Reference numerals 9 and 11 denote sampling ports. Reference numeral 10 denotes an adsorption column filled with an adsorbent, which detoxifies the decomposed gas and releases the detoxified gas from a release pipe 12.
【0017】以上、本発明に基づく装置の概要を示した
が、これらを一体となしたものは、コンパクトであり、
取扱いも容易で、効果的な排ガスの分解・無害化を可能
としたものである。The outline of the device according to the present invention has been described above, but a device in which these devices are integrated is compact,
It is easy to handle and enables effective decomposition and detoxification of exhaust gas.
【0018】[0018]
【実施例】以下に実施例、比較例、及び参考例により、
本発明をさらに具体的に説明する。
(実施例1〜6、比較例1〜4、及び参考例1)図1に
示す装置により実験を行った。分解器は外径38mm、
内径35mm、長さ1,000mmの高品位アルミナか
らなり、この中に分解剤500mlを充填し、電気加熱
した。吸着筒は内径3in、長さ300mmのPVC製
で、吸着剤を1200mlを充填した。吸着剤の調製は
ガスの種類に応じて以下の通り行った(A、B及び
C)。
有機フッ化物の場合:活性アルミナ及びソーダライム各
600mlに対して亜硫酸ナトリウム60mlの割合で
混合したもの(表1:A)
六フッ化硫黄の場合:ゼオライト及びソーダライム各6
00mlに対して亜硫酸ナトリウム60mlの割合で混
合したもの(表1:B)
三フッ化窒素の場合:活性アルミナ及びソーダライム各
600mlに対して、過マンガン酸カリウム60mlの
割合で混合したもの(表1:C)[Examples] The following examples , comparative examples, and reference examples
The present invention will be described more specifically. (Examples 1 to 6, Comparative Examples 1 to 4 , and Reference Example 1 ) Experiments were conducted using the apparatus shown in FIG. The decomposer has an outer diameter of 38 mm,
It was made of high-grade alumina having an inner diameter of 35 mm and a length of 1,000 mm, and 500 ml of a decomposing agent was filled in this and electrically heated. The adsorption column was made of PVC with an inner diameter of 3 inches and a length of 300 mm, and was filled with 1200 ml of an adsorbent. The adsorbent was prepared as follows according to the type of gas (A, B and C). Organic fluoride: 600 ml each of activated alumina and soda lime mixed with 60 ml of sodium sulfite (Table 1: A) Sulfur hexafluoride: 6 each of zeolite and soda lime
Mixture of 60 ml of sodium sulfite to 00 ml (Table 1: B) Nitrogen trifluoride: Mixture of 60 ml of potassium permanganate to 600 ml of activated alumina and soda lime (Table 1) 1: C)
【0019】実験中、定期的にサンプリングポート9、
11からサンプリングをし分解率及び排出ガス中の分解
により生じたフッ素及び塩素化合物の合計の濃度を測定
し、その濃度が1mg/l以上となった時点で実験を終
了した。実験条件及び結果を表1にまとめて示す。During the experiment, the sampling port 9 is regularly
The decomposition rate and the total concentration of fluorine and chlorine compounds produced by decomposition in the exhaust gas were measured by sampling from No. 11, and the experiment was terminated when the concentration became 1 mg / l or more. The experimental conditions and results are summarized in Table 1.
【0020】なお、フッ化水素を添加せずに、実施した
比較例では、分解率が低く、未分解の気体状フッ化物濃
度が高くなる。これら化合物は化学的に不活性で、吸着
剤では殆んど処理されない。吸着剤の処理量は分解生成
物の量によって決定されるので、比較例の方が実施時間
が長くなっていることが判る。In the comparative example carried out without adding hydrogen fluoride, the decomposition rate was low and the concentration of undecomposed gaseous fluoride was high. These compounds are chemically inert and rarely treated with adsorbents. Since the treatment amount of the adsorbent is determined by the amount of decomposition products, it can be seen that the comparative example has a longer execution time.
【0021】[0021]
【表1】 [Table 1]
【0022】[0022]
【発明の効果】分解剤にフッ化水素を併用することによ
り、分解効率が著しく向上し、排出ガスの安全化が容易
に達成され、さらには設備のコンパクト化が可能であ
る。EFFECTS OF THE INVENTION By using hydrogen fluoride in combination with the decomposing agent, the decomposition efficiency is remarkably improved, the safety of exhaust gas is easily achieved, and the equipment can be made compact.
【図1】本発明方法を実施するための装置の概略ブロッ
ク図。1 is a schematic block diagram of an apparatus for carrying out the method of the present invention.
1 気体状フッ化物供給ライン 2 フッ化水素供給ライン 3 分解剤供給装置 4 フッ化水素又は窒素供給ライン 5 分解器 6 電気加熱器 7 温度制御装置 8 冷却器 9、11 サンプリングポート 10 吸着筒 12 放出ライン 1 Gaseous fluoride supply line 2 Hydrogen fluoride supply line 3 Decomposing agent supply device 4 Hydrogen fluoride or nitrogen supply line 5 decomposer 6 electric heater 7 Temperature control device 8 cooler 9, 11 Sampling port 10 adsorption cylinder 12 emission line
───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平3−181316(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01D 53/68 ─────────────────────────────────────────────────── ─── Continuation of front page (56) Reference JP-A-3-181316 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B01D 53/68
Claims (2)
気体状フッ化物を含有する気体(フッ化水素を除く)を
フッ化水素の共存下、500℃〜1500℃の温度でS
i又はBの酸化物の内から選択された1種以上よりなる
分解剤と接触させることを特徴とする気体状フッ化物
(フッ化水素を除く)の分解方法。1. A gaseous fluoride (except hydrogen fluoride) or (except hydrogen fluoride) gas containing gaseous fluoride presence of hydrogen fluoride, S at a temperature of 500 ° C. to 1500 ° C.
A gaseous fluoride characterized by being brought into contact with a decomposing agent comprising one or more kinds selected from oxides of i or B.
Decomposition method (excluding hydrogen fluoride) .
ナ、ゼオライト、ソーダライム、シリカゲルの内から選
択された1種以上の吸着主剤と亜硫酸ナトリウム、チオ
硫酸ナトリウム、酸化マンガン/酸化銅、過マンガン酸
カリウムの内から選択された1種以上の吸着補助剤とか
らなる吸着剤と接触させる工程をさらに含む請求項1の
分解方法。2. The gas produced by the decomposition is treated with at least one adsorbent main agent selected from activated alumina, zeolite, soda lime and silica gel and sodium sulfite, sodium thiosulfate, manganese oxide / copper oxide, permanganate. The decomposition method according to claim 1, further comprising a step of contacting with an adsorbent composed of one or more adsorption aids selected from potassium.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP28110593A JP3490751B2 (en) | 1993-11-10 | 1993-11-10 | Decomposition method of gaseous fluoride |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP28110593A JP3490751B2 (en) | 1993-11-10 | 1993-11-10 | Decomposition method of gaseous fluoride |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH07132211A JPH07132211A (en) | 1995-05-23 |
| JP3490751B2 true JP3490751B2 (en) | 2004-01-26 |
Family
ID=17634425
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP28110593A Expired - Fee Related JP3490751B2 (en) | 1993-11-10 | 1993-11-10 | Decomposition method of gaseous fluoride |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3490751B2 (en) |
Families Citing this family (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6162957A (en) * | 1997-03-24 | 2000-12-19 | Showa Denko K.K. | Catalytic decomposition of perfluoro-compound |
| JP3593875B2 (en) * | 1997-03-24 | 2004-11-24 | 昭和電工株式会社 | Method for catalytic decomposition of perfluoro compounds |
| US6630421B1 (en) | 1999-04-28 | 2003-10-07 | Showa Denko Kabushiki Kaisha | Reactive agent and process for decomposing fluorine compounds and use thereof |
| JP4214717B2 (en) * | 2002-05-31 | 2009-01-28 | 株式会社日立製作所 | Perfluoride treatment equipment |
| EP1765485B1 (en) | 2004-07-08 | 2012-09-12 | Hyosung Corporation | Process for refining nitrogen trifluoride gas using alkali earth metal exchanged zeolite |
| EP1778387B1 (en) * | 2004-07-08 | 2012-09-12 | Hyosung Corporation | Process for refining nitrogen trifluoride gas using alkali earth metal exchanged and impregnated zeolite |
-
1993
- 1993-11-10 JP JP28110593A patent/JP3490751B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH07132211A (en) | 1995-05-23 |
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