JPS6111656B2 - - Google Patents
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- JPS6111656B2 JPS6111656B2 JP55045405A JP4540580A JPS6111656B2 JP S6111656 B2 JPS6111656 B2 JP S6111656B2 JP 55045405 A JP55045405 A JP 55045405A JP 4540580 A JP4540580 A JP 4540580A JP S6111656 B2 JPS6111656 B2 JP S6111656B2
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- Prior art keywords
- activated carbon
- coal
- gas
- flue gas
- inert gas
- Prior art date
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Description
【発明の詳細な説明】
本発明は排煙脱硫に使用された活性炭の再生工
程と、この再生工程でパージされるガス中のSO2
を石炭でイオウに還元する工程とを組み合わせ、
還元工程で副生されるセミコークス化石炭と、排
煙脱硫された燃焼排ガスとから実質的に酸素を含
まない不活性ガスを生成させ、この不活性ガスを
前記した再生工程の再生用ガスとして使用する排
煙脱硫用活性炭の再生法に係る。Detailed Description of the Invention The present invention relates to a regeneration process of activated carbon used in flue gas desulfurization, and a method for reducing SO 2 in the gas purged in this regeneration process.
Combined with the process of reducing sulfur to sulfur using coal,
An inert gas containing substantially no oxygen is generated from the semi-coked coal by-produced in the reduction process and the flue gas desulfurized, and this inert gas is used as the regeneration gas in the regeneration process described above. This relates to a method for regenerating activated carbon used for flue gas desulfurization.
固定発生源からの排ガスを脱硫する所謂排煙脱
硫法の一つとして、活性炭をイオウ酸化物の吸着
剤に使用し、活性炭と排ガスを接触させて排ガス
中のイオウ酸化物を活性炭に吸着させる方法が実
用化されている。この排煙脱硫法では、排ガスと
の接触により、次第にイオウ酸化物が活性炭上に
蓄積して活性炭の吸着能が衰微するため、適当な
時期にこれを再生してその吸着能を回復させなけ
ればならない。 As one of the so-called flue gas desulfurization methods for desulfurizing exhaust gas from fixed sources, activated carbon is used as an adsorbent for sulfur oxides, and the activated carbon is brought into contact with the exhaust gas to adsorb the sulfur oxides in the exhaust gas onto the activated carbon. has been put into practical use. In this flue gas desulfurization method, sulfur oxides gradually accumulate on the activated carbon due to contact with the exhaust gas, and the adsorption capacity of the activated carbon declines, so it is necessary to regenerate it at an appropriate time to restore its adsorption capacity. It won't happen.
吸着能が衰微した活性炭の再生は、例えば交流
移動床式再生器を使用し、活性炭を移動床状態に
保持してこれを間接的に加熱しながら活性炭の移
動床に酸素を含まない不活性ガスを接触させ、活
性炭からイオウ酸化物(主としてSO2)を脱離さ
せる方法で行なうことができる。そしてこの再生
時に得られるSO2含有ガスからは、これを石炭と
接触させてSO2をイオウに還元させることによ
り、単体イオウを回収することができる。 Activated carbon whose adsorption capacity has declined can be regenerated by using, for example, an AC moving bed regenerator, which maintains the activated carbon in a moving bed state and indirectly heats it while injecting oxygen-free inert gas into the moving bed of the activated carbon. This can be carried out by bringing sulfur oxides (mainly SO 2 ) into contact with activated carbon to remove sulfur oxides (mainly SO 2 ). From the SO 2 -containing gas obtained during this regeneration, elemental sulfur can be recovered by bringing it into contact with coal to reduce SO 2 to sulfur.
ところで、活性炭の再生時に必要な実質的に酸
素を含まない不活性ガスは、LPGなどのガス燃
料又は軽油などの液体燃料を空気量を調節しなが
ら燃焼させる方法、空気深冷による窒素ガス分
離法、酸素含有ガスのコークス層流通法、モ
レキユラーシーブによる酸素の吸着分離法、など
によつて得ることができる。しかし、の方法は
使用燃料が高価であるうえ、空気中に含まれる約
21%の酸素を消費する必要があることから、大量
の燃料を要して不経済であるという大きな欠点が
ある。の方法はこれを大規模に実施し、同時に
得られる酸素の有効利用が図れる場合には比較的
経済的であるが、空気の深冷分離器は排煙脱硫装
置の付帯設備としては一般的に不向きである。ま
たの方法は比較的小規模に窒素ガスを得るのに
は適しているものの、多量の窒素ガスを取得した
い場合には適さない。これに対しての方法は燃
焼排ガスの如く、比較的酸素濃度の低いガスを利
用することができ、従つてまたコークスの消費量
も少ないという利点がある。 By the way, the substantially oxygen-free inert gas required when regenerating activated carbon can be obtained by burning gaseous fuel such as LPG or liquid fuel such as light oil while adjusting the amount of air, or by nitrogen gas separation method using air deep cooling. , a coke bed flow method of oxygen-containing gas, a method of adsorption and separation of oxygen using a molecular sieve, and the like. However, in this method, the fuel used is expensive, and the amount of
The major drawback is that it requires a large amount of fuel and is uneconomical since it requires 21% of the oxygen consumed. This method is relatively economical if it is carried out on a large scale and at the same time the oxygen obtained can be used effectively. Not suitable. Although the method described above is suitable for obtaining nitrogen gas on a relatively small scale, it is not suitable for obtaining a large amount of nitrogen gas. This method has the advantage of being able to use a gas with a relatively low oxygen concentration, such as flue gas, and therefore also consuming less coke.
一方、活性炭の再生時に得られるSO2含有ガス
を、石炭と接触させてガス中のSO2をイオウに還
元する工程について考えると、活性炭の再生時に
得られるSO2含有ガスは、H2SO4・nH2O+1/2C
→1/2CO2+(n+1)H2Oなる再生反応式から理
解できるように、SO21モル当り(n+1)モル
もの水蒸気を含有するので、このガス中のSO2を
イオウに還元させる際には、水蒸気の存在に原因
するH2Sの副生を完全に回避することが極めて難
しい。従つて、活性炭の再生時に得られるSO2含
有ガスからイオウを回収せんとする場合には、石
炭とガスとの接触温度(反応温度)や滞留時間な
どを、適正にコントロールしてH2Sの副生をでき
る限り抑制する必要がある。そしてこの点に関し
て本発明者らが得た知見によれば、H2Sの副生を
抑えてSO2からSへの反応率を高めるためには、
反応器内の石炭が十分反応しないまま、換言すれ
ば石炭が完全にはコークス化していないセミコー
クス化の状態で、還元反応器から排出することが
肝要である。しかし、その場には石炭利用率が低
下するという不利がある。 On the other hand, considering the process of bringing SO 2 -containing gas obtained during activated carbon regeneration into contact with coal to reduce SO 2 in the gas to sulfur, the SO 2 -containing gas obtained during activated carbon regeneration is H 2 SO 4・nH2O +1/2C
→1/2CO 2 + (n+1)H 2 O As can be understood from the regeneration reaction formula, each 1 mole of SO 2 contains (n+1) moles of water vapor, so when reducing SO 2 in this gas to sulfur, It is extremely difficult to completely avoid the by-product of H 2 S caused by the presence of water vapor. Therefore, when attempting to recover sulfur from SO 2 -containing gas obtained during activated carbon regeneration, the contact temperature (reaction temperature) and residence time between coal and gas must be properly controlled to recover H 2 S. It is necessary to suppress by-products as much as possible. According to the knowledge obtained by the present inventors regarding this point, in order to suppress the by-product of H 2 S and increase the reaction rate from SO 2 to S,
It is important that the coal in the reactor is discharged from the reduction reactor without reacting sufficiently, in other words, in a semi-coked state in which the coal is not completely coked. However, there is a disadvantage in that the coal utilization rate decreases.
本発明は上記したセミコークス化石炭が活性炭
の再生に必要な不活性ガスを取得する場合の原料
として使用することができることに着目して、活
性炭の再生工程とSO2含有ガスの石炭による還元
工程とを組み合わせ、還元工程に於ける石炭利用
率の低下という不利益を解消させると共に、活性
炭再生用の不活性ガスを簡易に取得せんとするも
のである。 The present invention focuses on the fact that the above-mentioned semi-coked coal can be used as a raw material for obtaining the inert gas necessary for regenerating activated carbon, and the present invention has been developed in a process of regenerating activated carbon and reducing SO2- containing gas with coal. By combining these methods, the disadvantage of reduced coal utilization in the reduction process can be eliminated, and an inert gas for regenerating activated carbon can be easily obtained.
すなわち、本発明は排煙脱流に使用された活性
炭に不活性ガスを昇温下に接触させてSO2含有ガ
スを活性炭からパージさせる排煙脱硫用活性炭の
再生法に於て、
(a) 活性炭からパージされるSO2含有ガスを、移
動床式石炭充填塔に導入してSO2をイオウに還
元し、この還元反応で副生されるセミコークス
化した石炭を前記の石炭充填塔から取り出し、
(b) このセミコークス化石炭と、排煙脱硫された
燃焼排ガスとを不活性ガス発生炉に供給して、
当該発生炉から実質的に酸素を含まない不活性
ガスを生成させ、
(c) ここで得られた不活性ガスを排煙脱硫に使用
された活性炭の再生用ガスとして使用する、こ
とを特徴とする排煙脱硫用活性炭の再生法を提
供する。 That is, the present invention provides a method for regenerating activated carbon for flue gas desulfurization, in which activated carbon used for flue gas desulfurization is brought into contact with an inert gas at an elevated temperature to purge SO 2 -containing gas from the activated carbon. The SO 2 -containing gas purged from the activated carbon is introduced into a moving bed type coal-packed tower to reduce SO 2 to sulfur, and the semi-coked coal produced as a by-product of this reduction reaction is taken out from the coal-packed tower. , (b) supplying this semi-coked coal and flue gas desulfurized combustion flue gas to an inert gas generating furnace,
(c) The inert gas obtained here is used as a regeneration gas for activated carbon used in flue gas desulfurization. The present invention provides a method for regenerating activated carbon for flue gas desulfurization.
以下、添付図面にそつて本発明をさらに詳細に
説明すると、第1図は本発明方法を実施するのに
適したフローシートの一例を示すものであつて、
図中の1,4及び9はそれぞれ活性炭再生塔、移
動床式充填塔及び不活性ガス発生炉を示す。第1
図に於て、排煙脱硫に使用されてイオウ酸化物吸
着能が衰微した活性炭(以下、これを失活活性炭
という)は、再生塔1の頂部から塔内に供給され
る。活性炭再生塔1にはまた実質的に酸素を含ま
ない不活性ガス(この供給源については後述す
る)が管路2から導入され、300〜400℃という比
較的低温度で失活活性炭と接触する。この接触に
よつて失活活性炭は燃焼することなくSO2を放つ
て再生され、矢活活性炭から脱離したSO2は不活
性ガスによつて再生活性炭からパージされ、SO2
含有ガスとして管路3に取り出される。尚、図示
を省略したが、再生活性炭は通常連続的に再生塔
1から取り出されて排煙脱硫装置に送られ、ここ
で燃焼排ガス中のイオウ酸化物の吸着除去に再使
用できることは勿論である。 Hereinafter, the present invention will be explained in more detail with reference to the accompanying drawings. FIG. 1 shows an example of a flow sheet suitable for carrying out the method of the present invention.
Reference numerals 1, 4, and 9 in the figure indicate an activated carbon regeneration tower, a moving bed packed tower, and an inert gas generating furnace, respectively. 1st
In the figure, activated carbon (hereinafter referred to as deactivated activated carbon) that has been used for flue gas desulfurization and whose sulfur oxide adsorption ability has declined is fed into the regeneration tower 1 from the top thereof. Activated carbon regeneration tower 1 also receives a substantially oxygen-free inert gas (the source of which will be described below) through line 2, which contacts the deactivated activated carbon at a relatively low temperature of 300 to 400°C. . Through this contact, the deactivated activated carbon is regenerated by releasing SO 2 without burning, and the SO 2 desorbed from the activated carbon is purged from the regenerated activated carbon by an inert gas, and SO 2 is released.
It is taken out to the pipe line 3 as a contained gas. Although not shown, the regenerated activated carbon is usually continuously taken out from the regeneration tower 1 and sent to the flue gas desulfurization equipment, where it can of course be reused for adsorption and removal of sulfur oxides in the combustion flue gas. .
活性炭再生塔1から取り出されたSO2含有ガス
は、管路3を通つて移動床式石炭充填塔4に供給
される。当該充填塔4では塔頂部から供給される
石炭の移動床と、SO2含有ガスとが接触し、例え
ば特公昭54−36159号公報に記載された如き条件
で、ガス中のSO2は蒸気状の単体イオウに還元さ
れる。この還元反応に際しては、既述した通り、
還元剤たる石炭をセミコークス化の状態で充填塔
4底部から排出させることが、H2Sの副生を抑え
るうえで肝要であつて、一般には充填塔4内での
石炭の移動速度を調節することにより、石炭をセ
ミコークス化の状態で充填塔から排出することが
できる。充填塔4内での還元反応によつて生成し
た蒸気状単体イオウは、他のガスと共に管路5に
取り出されてイオウコンデンサー(図示なし)に
送られ、ここでイオウ回収が行なわれる。 The SO 2 -containing gas taken out from the activated carbon regeneration tower 1 is supplied to a moving bed type coal packed tower 4 through a pipe 3 . In the packed tower 4, the moving bed of coal supplied from the top of the tower comes into contact with the SO2 - containing gas, and under the conditions described in, for example, Japanese Patent Publication No. 54-36159, the SO2 in the gas is converted into vapor form. is reduced to elemental sulfur. As mentioned above, in this reduction reaction,
It is important to discharge coal, which is a reducing agent, from the bottom of the packed tower 4 in a semi-coked state in order to suppress the by-product of H 2 S, and generally the movement speed of the coal within the packed tower 4 is adjusted. By doing so, the coal can be discharged from the packed tower in a semi-coked state. The vaporized elemental sulfur produced by the reduction reaction in the packed column 4 is taken out along with other gases into a pipe 5 and sent to a sulfur condenser (not shown), where sulfur is recovered.
一方、セミコークス化の状態で充填塔4の底部
から管路7に排出される石炭は、篩分け機7で灰
分などを除去した後、管路8を経由して不活性ガ
ス発生炉9にその頂部から導入され、炉内で移動
床を形成する。そしてこの不活性ガス発生炉9に
は、排煙脱硫された燃焼排ガスが管路10から供
給される。この燃焼排ガスは昇温下にセミコーク
ス化石炭と接触して不活化する。つまり、当該排
ガスに含まれる実質的にすべての酸素が、セミコ
ークス化石炭との接触によつて消費されるのであ
る。ちなみに、燃焼排ガス中の酸素濃度は、ボイ
ラー排ガスを例にとれば、石炭ボイラーで3〜8
%、重油専焼ボイラーで1〜6%であつて、この
値は各ボイラーの負荷変動によつて50〜100%の
範囲で変動する。しかしそうした場合でも、必要
に応じて補助空気を制御された量で不活性ガス発
生炉9に供給して、炉内温度を600〜900℃、好ま
ししくは700〜800℃に維持することにより、炉内
に供給される実質的にすべての酸素を消費するこ
とができる。こうして得られた実質的に酸素を含
まない不活性ガスは、不活性ガス発生炉9から管
路2に取り出され、活性炭再生塔1に供給され
る。 On the other hand, the coal discharged from the bottom of the packed tower 4 into the pipe 7 in a semi-coked state is passed through the sieve 7 to remove ash, etc., and then sent to the inert gas generating furnace 9 via the pipe 8. It is introduced from the top and forms a moving bed within the furnace. The inert gas generating furnace 9 is supplied with flue gas desulfurized from a pipe 10 . This combustion exhaust gas comes into contact with semi-coked coal under elevated temperature and is inactivated. That is, substantially all the oxygen contained in the exhaust gas is consumed by contact with the semi-coked coal. By the way, taking boiler exhaust gas as an example, the oxygen concentration in combustion exhaust gas is 3 to 8 in a coal boiler.
%, and is 1 to 6% for heavy oil-fired boilers, and this value fluctuates in the range of 50 to 100% depending on load fluctuations of each boiler. However, even in such a case, by supplying auxiliary air in a controlled amount to the inert gas generating furnace 9 as necessary to maintain the furnace temperature at 600 to 900°C, preferably 700 to 800°C. , can consume virtually all the oxygen supplied into the furnace. The substantially oxygen-free inert gas thus obtained is taken out from the inert gas generating furnace 9 into the pipe line 2 and supplied to the activated carbon regeneration tower 1.
尚、不活性ガス発生炉9ではセミコークス化石
炭が炉出口で丁度灰分になるように、その移動速
度を制御することも可能であるが、灰化によるト
ラブルを避けるために、セミコークス化石炭が残
存する状態で炉出口から排出されるよう制御し、
図示の通り、管路11に出るセミコークス化石炭
を篩分け機7に通して灰分の除去を行なつた後、
管路8経由で不活性ガス発生炉9に循環した方
が、より安定した操業を行なうことができる。 In addition, in the inert gas generating furnace 9, it is possible to control the movement speed of the semi-coked coal so that it turns into ash at the furnace outlet, but in order to avoid troubles due to ashing, it is possible to control the movement speed of the semi-coked coal control so that it is discharged from the furnace outlet in a state where it remains,
As shown in the figure, after the semi-coked coal coming out of the pipe 11 is passed through a sieve 7 to remove ash,
Circulating to the inert gas generating furnace 9 via the pipe line 8 allows for more stable operation.
第2図は本発明を実施する場合の別のフローを
示すものであつて、本例では活性炭再生塔1に付
設される関接熱交換器20に燃焼排ガスを供給
し、活性炭再生塔に熱を付与して熱交換器20か
ら管路21に排出される燃焼排ガスを、不活性ガ
ス発生炉9に供給する。そして篩分け機7で灰分
を除去後、管路8で不活性ガス発生炉9へ送られ
るセミコークス化石炭の一部を、管路22に分流
させて移動床式石炭充填塔4に供給する。その他
は第1図に示すフローと同一である。 FIG. 2 shows another flow when implementing the present invention. In this example, combustion exhaust gas is supplied to the indirect heat exchanger 20 attached to the activated carbon regeneration tower 1, and the activated carbon regeneration tower receives heat. The combustion exhaust gas discharged from the heat exchanger 20 to the pipe line 21 is supplied to the inert gas generating furnace 9. After removing ash in the sieving machine 7, a part of the semi-coked coal is sent to the inert gas generating furnace 9 through a pipe line 8, and is then diverted to a pipe line 22 and supplied to the moving bed type coal packed tower 4. . The rest of the flow is the same as the flow shown in FIG.
第2図のフローに従えば、活性炭再生器1に熱
を与えて熱交換器20から温度約300〜350℃で排
出される燃焼排ガスを不活性ガス発生炉に供給で
きるので、不活性ガス発生炉内の温度制御が容易
になる利点がある。これに加えて、セミコークス
化石炭の移動床式石炭充填塔での再利用が図れる
ので、全体として石炭が無駄なく使用できる利点
もある。 If you follow the flow shown in Figure 2, you can supply heat to the activated carbon regenerator 1 and the combustion exhaust gas discharged from the heat exchanger 20 at a temperature of about 300 to 350°C to the inert gas generation furnace. This has the advantage of making it easier to control the temperature inside the furnace. In addition, since the semi-coked coal can be reused in the moving bed type coal-filled tower, there is also the advantage that the coal can be used without wasting it as a whole.
以上説明して来たところから明らかな通り、本
発明によれば、SO2をイオウに還元する際に副生
されるセミコークス化石炭を利用して、活性炭の
再生に必要な不活性ガスを生成させることができ
るのである。 As is clear from the above explanation, according to the present invention, the inert gas necessary for regenerating activated carbon can be produced by using semi-coked coal, which is produced as a by-product when reducing SO 2 to sulfur. It can be generated.
第1図及び第2図は本発明方法を実施する場合
のフローシートの一例を示す。
1;活性炭再生塔、2;不活性ガス管路、3;
SO2含有ガス管路、4;移動床式石炭充填塔、
7;篩分け機、8;セミコークス化石炭管路、
9;不活性ガス発生炉、10;燃焼排ガス管路、
20;間接熱交換器、21;燃焼排ガス管路、2
2;セミコークス化石炭分流管路。
FIGS. 1 and 2 show an example of a flow sheet for carrying out the method of the present invention. 1; Activated carbon regeneration tower, 2; Inert gas pipe, 3;
SO2 - containing gas pipe, 4; moving bed coal-filled tower,
7; Sieving machine, 8; Semi-coked coal pipeline,
9; Inert gas generator, 10; Combustion exhaust gas pipe,
20; indirect heat exchanger, 21; combustion exhaust gas pipe, 2
2; Semi-coked coal distribution pipe.
Claims (1)
昇温下に接触させてSO2含有ガスを活性炭からパ
ージさせる排煙脱硫用活性炭の再生法に於て、 (a) 活性炭からパージされるSO2含有ガスを、移
動床式石炭充填塔に導入してSO2をイオウに還
元し、この還元反応で副生されるセミコークス
化した石炭を前記の石炭充填塔から取り出し、 (b) このセミコークス化石炭と、排煙脱硫された
燃焼排ガスとを不活性ガス発生炉に供給して、
当該発生炉から実質的に酸素を含まない不活性
ガスを生成させ、 (c) ここで得られた不活性ガスを排煙脱硫に使用
された活性炭の再生用ガスとして使用する。 ことを特徴とする排煙脱硫用活性炭の再生法。[Claims] 1. In a method for regenerating activated carbon for flue gas desulfurization, in which activated carbon used for flue gas desulfurization is brought into contact with an inert gas at an elevated temperature to purge SO 2 -containing gas from the activated carbon, (a ) The SO 2 -containing gas purged from the activated carbon is introduced into a moving bed type coal-packed tower to reduce SO 2 to sulfur, and the semi-coked coal produced as a by-product of this reduction reaction is transferred from the coal-packed tower. (b) supplying this semi-coked coal and flue gas desulfurized combustion flue gas to an inert gas generating furnace;
(c) The inert gas obtained here is used as a regeneration gas for activated carbon used in flue gas desulfurization. A method for regenerating activated carbon for flue gas desulfurization, characterized by:
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4540580A JPS56141816A (en) | 1980-04-07 | 1980-04-07 | Method for reactivating activated carbon for desulfurization of combustion gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4540580A JPS56141816A (en) | 1980-04-07 | 1980-04-07 | Method for reactivating activated carbon for desulfurization of combustion gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS56141816A JPS56141816A (en) | 1981-11-05 |
| JPS6111656B2 true JPS6111656B2 (en) | 1986-04-04 |
Family
ID=12718336
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP4540580A Granted JPS56141816A (en) | 1980-04-07 | 1980-04-07 | Method for reactivating activated carbon for desulfurization of combustion gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS56141816A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0514055U (en) * | 1991-08-09 | 1993-02-23 | コクヨ株式会社 | Tape cutter |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5835920U (en) * | 1981-09-02 | 1983-03-09 | バブコツク日立株式会社 | Dry desulfurization equipment |
| JPS58114715A (en) * | 1981-12-26 | 1983-07-08 | Sumitomo Heavy Ind Ltd | Formation of inert gas in dry desulfurizer |
| CN106166431B (en) * | 2016-08-29 | 2019-04-12 | 江苏江大环境工程有限责任公司 | A kind of active carbon thermopnore adsorption combined device containing dust and organic exhaust gas |
-
1980
- 1980-04-07 JP JP4540580A patent/JPS56141816A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0514055U (en) * | 1991-08-09 | 1993-02-23 | コクヨ株式会社 | Tape cutter |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS56141816A (en) | 1981-11-05 |
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