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JPH0711114B2 - Soda recovery method - Google Patents
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JPH0711114B2 - Soda recovery method - Google Patents

Soda recovery method

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Publication number
JPH0711114B2
JPH0711114B2 JP61113340A JP11334086A JPH0711114B2 JP H0711114 B2 JPH0711114 B2 JP H0711114B2 JP 61113340 A JP61113340 A JP 61113340A JP 11334086 A JP11334086 A JP 11334086A JP H0711114 B2 JPH0711114 B2 JP H0711114B2
Authority
JP
Japan
Prior art keywords
iron oxide
fluidized bed
nacl
causticizing
dust collector
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.)
Expired - Lifetime
Application number
JP61113340A
Other languages
Japanese (ja)
Other versions
JPS62268883A (en
Inventor
速水 伊東
千秋 永井
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kawasaki Motors Ltd
Original Assignee
Kawasaki Jukogyo KK
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Kawasaki Jukogyo KK filed Critical Kawasaki Jukogyo KK
Priority to JP61113340A priority Critical patent/JPH0711114B2/en
Publication of JPS62268883A publication Critical patent/JPS62268883A/en
Publication of JPH0711114B2 publication Critical patent/JPH0711114B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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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、パルプ蒸解廃液(黒液ともいう)から酸化鉄
を苛性化剤として苛性ソーダを回収する直接苛性化法流
動床方式において、不純物を除去する方法、詳しくは集
じん機捕集物を冷水抽出し、NaCl含有廃液を系外に排出
することにより、NaClを系内に蓄積させないようにした
ソーダ回収方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention relates to a direct causticizing fluidized bed system for recovering caustic soda from pulp cooking waste liquor (also referred to as black liquor) using iron oxide as a causticizing agent to remove impurities. More specifically, the present invention relates to a soda recovery method in which NaCl collected in the dust collector is extracted with cold water and the NaCl-containing waste liquid is discharged to the outside of the system to prevent NaCl from accumulating in the system.

〔従来の技術〕[Conventional technology]

従来、木材チップを蒸解したときに発生するパルプ蒸解
廃液(以下、パルプ廃液という)から苛性ソーダを回収
する場合、石灰法が実用化されている。しかしこの石灰
法は工程が複雑であり、また廃物を生じるので臭気対
策、排水対策が必要であり、苛性化率が悪いなどの欠点
を有していた。
Conventionally, when recovering caustic soda from pulp cooking waste liquid (hereinafter referred to as pulp waste liquid) generated when wood chips are digested, the lime method has been put into practical use. However, this lime method has drawbacks in that the process is complicated, waste is generated, and measures against odor and drainage are required, and the causticizing rate is low.

これらの欠点を解消するために、特公昭51-12724号公報
に開示されるように、繊維素物質の蒸解および漂白工程
より排出される実質的に硫黄化合物を含まないアルカリ
廃液を、濃縮後酸化鉄を加えて燃焼せしめ、得られた鉄
酸ソーダ(鉄酸ナトリウム)を水中に投入して抽出水溶
液として直接苛性ソーダを回収するとともに、抽出残渣
として得られた酸化鉄を循環再使用する方法が提案され
ている。この方法では、アルカリ廃液からの苛性ソーダ
の生成は、おそらく廃液の燃焼によって廃液中に含まれ
ていた有機物は分解し、生成物として得られた炭酸ソー
ダおよび/または酸化ソーダが下記の(1)式および
(2)式の如く酸化鉄と反応して鉄酸ソーダを生成し、
これを水中で処理することによって(3)式の如く、苛
性ソーダと酸化鉄が得られるものと考えられる。
In order to eliminate these drawbacks, as disclosed in Japanese Patent Publication No. 51-12724, the alkaline waste liquid containing substantially no sulfur compounds discharged from the cooking and bleaching steps of the fibrin substance is concentrated and oxidized. A method is proposed in which iron is added and burned, the resulting sodium ferrate (sodium ferrate) is put into water to directly recover caustic soda as an extraction aqueous solution, and the iron oxide obtained as an extraction residue is circulated and reused. Has been done. In this method, caustic soda is produced from an alkaline waste liquid, organic matter contained in the waste liquid is decomposed by combustion of the waste liquid, and sodium carbonate and / or sodium oxide obtained as a product is expressed by the following formula (1). And as in formula (2), reacts with iron oxide to produce sodium ferrate,
It is considered that by treating this in water, caustic soda and iron oxide can be obtained as shown in formula (3).

Na2CO3+Fe2O3→Na2Fe2O4+CO2 (1) Na2O+Fe2O3→Na2Fe2O4 (2) Na2Fe2O4+H2O→2NaOH+Fe2O3 (3) しかし上記の方法を流動床炉に適用するにあたり、直接
苛性化法では、酸化鉄(鉄鉱石)は再生循環使用するの
が大原則であり、集じん機などのキャリーオーバー分の
み補給する(補給率は高々数%のオーダーである)。一
方、苛性化反応剤であると同時に流動層維持剤である粒
状鉄鉱石は再生使用回数の増加に従い、炉内での粉化が
増大すること(約10%前後は粉化)、その他フィーダー
での鉄鉱石のハンドリング、苛性化工程などでも若干粉
化が見られる。また流動床方式では基本的に粒状の苛性
化剤を使用するため、反応モル比Fe/Naを1.0近くに設定
することができず(反応式(1)、(2)に示すように
等モル反応)、一方、粉状の苛性化剤では炉内からすぐ
飛び出してしまい反応の進行が十分期待できないなどの
問題があった。
Na 2 CO 3 + Fe 2 O 3 → Na 2 Fe 2 O 4 + CO 2 (1) Na 2 O + Fe 2 O 3 → Na 2 Fe 2 O 4 (2) Na 2 Fe 2 O 4 + H 2 O → 2NaOH + Fe 2 O 3 (3) However, when applying the above method to a fluidized bed furnace, it is a general principle to recycle iron oxide (iron ore) in the direct causticizing method. Replenish only for carryover such as (the replenishment rate is at the order of several% at most). On the other hand, granular iron ore, which is both a causticizing agent and a fluidized bed maintainer, increases the pulverization in the furnace as the number of times of re-use increases (about 10% pulverization), and other feeders Some pulverization is also seen in the handling of iron ore, causticizing process, etc. Further, in the fluidized bed system, since a granular causticizing agent is basically used, the reaction molar ratio Fe / Na cannot be set near 1.0 (equal molar ratio as shown in reaction formulas (1) and (2)). On the other hand, there is a problem that the powdery causticizing agent jumps out of the furnace immediately and the reaction cannot be expected to proceed sufficiently.

本発明者らは上記の問題点を解決するために、流動床ボ
イラ、サイクロン、電気集じん機で捕集された粉状鉄酸
ソーダを苛性化した後、乾燥し、乾燥した粉状酸化鉄の
一部あるいは全部を黒液をバインダーとして造粒し、再
び粒状物として流動床炉に供給する技術を開発し、特願
昭58-167927号(特開昭60-59190号)として特許出願し
ている。
In order to solve the above problems, the present inventors causticize powdered sodium iron oxide collected by a fluidized bed boiler, a cyclone, and an electrostatic precipitator, and then dry the dried powdered iron oxide. We developed a technology to granulate a part or all of the product using a black liquor as a binder and then supply it to the fluidized bed furnace as granules again. ing.

〔発明が解決しようとする問題点〕[Problems to be solved by the invention]

上記の直接苛性化法は、KP法に比較して、石灰キルンを
省略し、プロセスの簡略化、省エネルギー化を目指した
優れたプロセスであるが、クローズド化を特徴とする点
に問題がある。
Compared to the KP method, the direct causticizing method is an excellent process aiming at simplifying the process and energy saving by omitting the lime kiln, but has a problem in that it is closed.

すなわち、製紙プロセスにおいては、木材チップ、工業
用水などにより、蒸解に必要な薬液以外の不純物が入り
込む。KP法では、ドレッグ、スラッジなどとともに、不
純物は沈澱物として系外に投棄されるのに対し、直接苛
性化法では系がクローズド化されているので、系外から
侵入した不純物は、系内で次第に濃縮される傾向にあ
る。この内、NaClは鉄酸ソーダ生成反応に悪影響を与え
る(反応阻害となる)、Na2CO3と低温域にて溶融する共
融混合物をつくり易いなど、直接苛性化法流動床式に悪
影響を与える。
That is, in the papermaking process, impurities other than the chemical liquid necessary for cooking enter due to wood chips, industrial water, and the like. In the KP method, impurities such as dregs and sludge are discarded as a precipitate out of the system, whereas in the direct causticization method, the system is closed. It tends to be gradually concentrated. Of these, NaCl has a negative effect on the sodium ferrate formation reaction (restricts the reaction), and it is easy to form a eutectic mixture that melts with Na 2 CO 3 in the low temperature range, which adversely affects the direct causticizing fluidized bed system. give.

本発明は上記の諸点に鑑みなされたもので、NaClを系内
に蓄積させないで、一定の値以下にその濃度を制御し、
効率よく苛性ソーダを回収できるようにした方法の提供
を目的とするものである。
The present invention has been made in view of the above points, without accumulating NaCl in the system, the concentration is controlled below a certain value,
It is intended to provide a method capable of efficiently collecting caustic soda.

〔問題点を解決するための手段および作用〕[Means and Actions for Solving Problems]

本願の第1の発明のソーダ回収方法は、NaClを含むパル
プ廃液を、酸化鉄を苛性化剤および流動化媒体とする流
動床炉で燃焼せしめ、ついで生成物である鉄酸ソーダを
水中に投入して苛性ソーダおよび酸化鉄を回収し、流動
床炉排ガスをボイラで熱回収した後、サイクロン、電気
集じん機に導入して集じんする方法において、電気集じ
ん機捕集物を冷水抽出し、NaCl含有廃液を系外に排出
し、粉状酸化鉄を苛性化工程または乾燥工程に導入する
ことを特徴としている。
The soda recovery method of the first invention of the present application is to burn a pulp waste liquid containing NaCl in a fluidized bed furnace using iron oxide as a causticizing agent and a fluidizing medium, and then add the product sodium ferrate to water. Then, the caustic soda and iron oxide are recovered, the fluidized bed furnace exhaust gas is heat-recovered by the boiler, and then the cyclone is introduced into an electric dust collector to collect dust, and the collected electricity dust collector is extracted with cold water. The feature is that the NaCl-containing waste liquid is discharged to the outside of the system, and the powdery iron oxide is introduced into the causticizing process or the drying process.

すなわち、ボイラ後流以降の集じん装置としては、マル
チサイクロンなどのサイクロン、電気集じん機などが用
いられ、煙道捕集粉状鉄酸ソーダのうち、NaCl含有量の
最も高い電気集じん機捕集物を冷水抽出し、NaCl含有廃
液を系外に投棄することにより、系内にNaClを蓄積させ
ることなく、流動床方式を好適に運転することができ
る。
That is, as a dust collector after the boiler, a cyclone such as a multi-cyclone, an electric dust collector, etc. are used, and among the flue trapped powdery sodium ferrate, the dust collector with the highest NaCl content is used. By extracting the collected matter with cold water and discarding the NaCl-containing waste liquid to the outside of the system, it is possible to suitably operate the fluidized bed system without accumulating NaCl in the system.

また本願の第2の発明のソーダ回収方法は、NaCl含有量
の高い電気集じん機捕集物の全部、およびNaCl含有量の
高いサイクロン捕集物の一部または全部を冷水抽出し、
NaCl含有廃液を系外に排出し、粉状酸化鉄を苛性化工程
または乾燥工程に導入することを特徴としており、これ
により系内にNaClを蓄積させることなく、流動床方式を
好適に運転することができる。
The second invention soda recovery method of the present application, cold water extraction of all of the electrostatic precipitator trap with high NaCl content, and part or all of the cyclone trap with high NaCl content,
It is characterized by discharging the NaCl-containing waste liquid to the outside of the system and introducing the powdered iron oxide into the causticizing process or the drying process, which allows the fluidized bed system to operate properly without accumulating NaCl in the system. be able to.

サイクロン捕集物、電気集じん機捕集物のNaClの割合
は、通常、重量比で全ソーダ分の10〜70%であり、電気
集じん機捕集物では、Naの50%以上はNaClの形で含有さ
れている。
The ratio of NaCl in the cyclone collected matter and the electric dust collector collected is usually 10 to 70% by weight of the total soda, and in the electric dust collector collected, 50% or more of Na is NaCl. It is contained in the form of.

〔実施例〕〔Example〕

以下、本発明の実施例を図面に基づいて例示的に詳細に
説明する。ただしこの実施例に記載されている構成機器
の配置などは、とくに特定的な記載がない限りは、それ
らのみに限定するものではなく、単なる説明例にすぎな
い。
Hereinafter, embodiments of the present invention will be illustratively described in detail with reference to the drawings. However, the arrangement of the constituent devices described in this embodiment is not limited to them unless otherwise specified, and is merely an example of description.

希黒液を薄膜式エバポレータ1に導入し、蒸発、濃縮し
て50〜60%の黒液とした後、ディスクエバポレータ2に
導入して70〜80%の濃黒液とし、この濃黒液を流動床炉
3に供給する。一方、流動床炉3に粒状鉄鉱石貯槽4か
ら粒状酸化鉄を供給する。流動床炉3の層温度は700〜1
100℃、望ましくは900〜1000℃とし、Fe/Naは1.0以上と
なるようにする。流動層形成材としては、純鉄、鉄鉱石
(Fe2O3、Fe3O4)、焼結鉱、還元ペレット、製鉄ダスト
を造粒したものなどの粒状の鉄系の粒状の化合物が用い
られる。本例においては、酸化鉄として鉄鉱石を使用
し、補給は粒状鉄鉱石で行う。5は流動層、6は空気分
散板、7は風箱である。
The diluted black liquor is introduced into the thin film evaporator 1, evaporated and concentrated to 50-60% black liquor, and then introduced into the disc evaporator 2 to obtain 70-80% dark liquor. It is supplied to the fluidized bed furnace 3. On the other hand, granular iron ore storage tank 4 supplies granular iron oxide to fluidized bed furnace 3. Bed temperature of fluidized bed furnace 3 is 700-1
The temperature is 100 ° C., preferably 900 to 1000 ° C., and the Fe / Na is 1.0 or more. As the fluidized bed forming material, granular iron-based granular compounds such as pure iron, iron ore (Fe 2 O 3 , Fe 3 O 4 ), sinter ore, reduced pellets, and granulated iron-making dust are used. To be In this example, iron ore is used as iron oxide, and the replenishment is performed with granular iron ore. 5 is a fluidized bed, 6 is an air dispersion plate, and 7 is a wind box.

流動床炉3からの鉄酸ソーダを第1苛性化装置8に導入
して苛性ソーダ水溶液と回収酸化鉄とに抽出、分離し、
この回収酸化鉄を第1乾燥装置10で燃焼排ガスなどによ
り乾燥した後、分級装置11で粒状酸化鉄と粉状酸化鉄と
に分級し、粒状酸化鉄を粒状鉄鉱石貯槽4に投入し、一
方、粉状酸化鉄を造粒装置12および粉状酸化鉄貯槽13へ
供給する。この造粒装置としては、圧縮造粒装置とする
のが好ましい。
Sodium ferrate from the fluidized bed furnace 3 is introduced into the first causticizing device 8 to extract and separate into a caustic soda aqueous solution and recovered iron oxide,
After the recovered iron oxide is dried by combustion exhaust gas in the first drying device 10, it is classified into granular iron oxide and powdered iron oxide by the classifying device 11, and the granular iron oxide is charged into the granular iron ore storage tank 4, while The powdery iron oxide is supplied to the granulating device 12 and the powdery iron oxide storage tank 13. As this granulating device, a compression granulating device is preferable.

一方、ボイラ14で捕集した粉状捕集物を第2苛性化装置
15へ導入して苛性ソーダ水溶液と回収酸化鉄とに抽出、
分離し、この回収酸化鉄を第2乾燥装置16で燃焼排ガス
などにより乾燥した後、造粒装置12で黒液をバインダー
として造粒して粒状酸化鉄とし鉄鉱石貯槽4へ投入す
る。
On the other hand, the powdery collected matter collected by the boiler 14 is used as the second causticizing device.
Introduced into 15 and extracted into aqueous caustic soda solution and recovered iron oxide,
The separated iron oxide is separated and dried in the second drying device 16 by combustion exhaust gas or the like, and then, in the granulating device 12, the black liquor is granulated as a binder to form granular iron oxide into the iron ore storage tank 4.

電気集じん機18の捕集物の全部、または電気集じん機18
の捕集物の全部とサイクロン17の捕集物の一部もしくは
全部とを、冷水抽出装置20へ供給して冷水抽出し、NaCl
含有廃液を系外に排出して系内にNaClが蓄積するのを防
止し、冷水抽出後の微細な酸化鉄を第2苛性化装置15ま
たは第2乾燥装置16へ導入する。
All of the collected matter of the electric dust collector 18 or the electric dust collector 18
All of the collected substances of (1) and a part or all of the collected substances of the cyclone (17) are supplied to the cold water extraction device (20) for cold water extraction, and NaCl is extracted.
The contained waste liquid is discharged to the outside of the system to prevent NaCl from accumulating in the system, and the fine iron oxide after cold water extraction is introduced into the second causticizing device 15 or the second drying device 16.

このように、NaCl含有率の最も高い電気集じん機捕集物
は、全量冷水抽出する。サイクロン捕集物は全量冷水抽
出する場合と、一部を冷水抽出する場合と、全量を冷水
抽出しない場合とがある。
Thus, the whole amount of the electrostatic precipitator trap having the highest NaCl content is extracted with cold water. There are cases where the whole cyclone is extracted with cold water, a case where a part is extracted with cold water, and a case where the whole is not extracted with cold water.

サイクロン捕集物で冷水抽出しない分は、第2苛性化装
置15または第2乾燥装置16へそのまま供給する。
The portion of the cyclone collected product that is not extracted with cold water is directly supplied to the second causticizing device 15 or the second drying device 16.

〔発明の効果〕〔The invention's effect〕

上記のように本発明の方法によれば、NaClを系内に蓄積
させないで、一定のレベル以下にその濃度をコントロー
ルし、苛性化反応を好適に進行させるとともに、酸化
鉄、鉄酸ソーダを流動化媒体とする流動層を、良好な流
動化状態を保つことが可能になるという効果を奏する。
As described above, according to the method of the present invention, NaCl is not accumulated in the system, its concentration is controlled to a certain level or less, and the causticizing reaction is appropriately advanced, and iron oxide and sodium ferrate are allowed to flow. The fluidized bed used as the fluidizing medium can maintain an excellent fluidized state.

【図面の簡単な説明】[Brief description of drawings]

図面は本発明のソーダ回収方法を実施する装置の一例を
示すフローシートである。 1……薄膜式エバポレータ、2……ディスクエバポレー
タ、3……流動床炉、4……粒状鉄鉱石貯槽、5……流
動層、6……空気分散板、7……風箱、8……第1苛性
化装置、10……第1乾燥装置、11……分級装置、12……
造粒装置、13……粉状酸化鉄貯槽、14……ボイラ、15…
…第2苛性化装置、16……第2乾燥装置、17……サイク
ロン、18……電気集じん機、20……冷水抽出装置
The drawings are flow sheets showing an example of an apparatus for carrying out the soda recovery method of the present invention. 1 ... Thin film evaporator, 2 ... Disk evaporator, 3 ... Fluidized bed furnace, 4 ... Granular iron ore storage tank, 5 ... Fluidized bed, 6 ... Air dispersion plate, 7 ... Wind box, 8 ... 1st causticizing device, 10 ... 1st drying device, 11 ... Classifying device, 12 ...
Granulator, 13 …… Powdery iron oxide storage tank, 14 …… Boiler, 15…
… Second causticizer, 16 …… Second dryer, 17 …… Cyclone, 18 …… Electrostatic precipitator, 20 …… Cold water extractor

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】NaClを含むパルプ廃液を、酸化鉄を苛性化
剤および流動化媒体とする流動床炉で燃焼せしめ、つい
で生成物である鉄酸ソーダを水中に投入して苛性ソーダ
および酸化鉄を回収し、流動床炉排ガスをボイラで熱回
収した後、サイクロン、電気集じん機に導入して集じん
する方法において、電気集じん機捕集物を冷水抽出し、
NaCl含有廃液を系外に排出し、粉状酸化鉄を苛性化工程
または乾燥工程に導入することを特徴とするソーダ回収
方法。
1. A pulp waste liquor containing NaCl is combusted in a fluidized bed furnace using iron oxide as a causticizing agent and a fluidizing medium, and then the product sodium ferrate is put into water to remove caustic soda and iron oxide. After collecting and recovering the heat of the fluidized bed furnace exhaust gas with a boiler, in a method of introducing dust into a cyclone and an electric dust collector, the collected matter of the electric dust collector is extracted with cold water,
A soda recovery method comprising discharging a NaCl-containing waste liquid to the outside of the system and introducing powdered iron oxide into a causticizing step or a drying step.
【請求項2】NaClを含むパルプ廃液を、酸化鉄を苛性化
剤および流動化媒体とする流動床炉で燃焼せしめ、つい
で生成物である鉄酸ソーダを水中に投入して苛性ソーダ
および酸化鉄を回収し、流動床炉排ガスをボイラで熱回
収した後、サイクロン、電気集じん機に導入して集じん
する方法において、電気集じん機捕集物の全部、および
サイクロン捕集物の一部または全部を冷水抽出し、NaCl
含有廃液を系外に排出し、粉状酸化鉄を苛性化工程また
は乾燥工程に導入することを特徴とするソーダ回収方
法。
2. A pulp waste liquor containing NaCl is combusted in a fluidized bed furnace using iron oxide as a causticizing agent and a fluidizing medium, and then the product sodium ferrate is put into water to remove caustic soda and iron oxide. In the method of recovering and collecting the heat of the fluidized bed furnace exhaust gas with a boiler, and then introducing it into a cyclone or an electric dust collector to collect dust, all of the collected matter of the electric dust collector and a part of the collected matter of the cyclone or Extract all with cold water and add NaCl
A soda recovery method comprising discharging the contained waste liquid to the outside of the system and introducing the powdered iron oxide into a causticizing step or a drying step.
JP61113340A 1986-05-16 1986-05-16 Soda recovery method Expired - Lifetime JPH0711114B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61113340A JPH0711114B2 (en) 1986-05-16 1986-05-16 Soda recovery method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61113340A JPH0711114B2 (en) 1986-05-16 1986-05-16 Soda recovery method

Publications (2)

Publication Number Publication Date
JPS62268883A JPS62268883A (en) 1987-11-21
JPH0711114B2 true JPH0711114B2 (en) 1995-02-08

Family

ID=14609763

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61113340A Expired - Lifetime JPH0711114B2 (en) 1986-05-16 1986-05-16 Soda recovery method

Country Status (1)

Country Link
JP (1) JPH0711114B2 (en)

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5522051A (en) * 1978-08-02 1980-02-16 Tokuyama Soda Kk Desalting method
JPS58132192A (en) * 1982-01-27 1983-08-06 バブコツク日立株式会社 Direct caustification using fluidized layer furnace
JPS5943186A (en) * 1982-08-30 1984-03-10 バブコツク日立株式会社 Combustion of black liquor
JPS6081015A (en) * 1983-10-12 1985-05-09 Babcock Hitachi Kk Direct causticizing method using fluidized bed

Also Published As

Publication number Publication date
JPS62268883A (en) 1987-11-21

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