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JPS5951340B2 - Method for producing particulate inorganic ion exchanger - Google Patents
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JPS5951340B2 - Method for producing particulate inorganic ion exchanger - Google Patents

Method for producing particulate inorganic ion exchanger

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Publication number
JPS5951340B2
JPS5951340B2 JP53081563A JP8156378A JPS5951340B2 JP S5951340 B2 JPS5951340 B2 JP S5951340B2 JP 53081563 A JP53081563 A JP 53081563A JP 8156378 A JP8156378 A JP 8156378A JP S5951340 B2 JPS5951340 B2 JP S5951340B2
Authority
JP
Japan
Prior art keywords
ion exchanger
acid
water
inorganic ion
moles
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
Application number
JP53081563A
Other languages
Japanese (ja)
Other versions
JPS558844A (en
Inventor
宏 佐藤
定明 重田
廣幸 内田
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.)
Mitsubishi Chemical Corp
Original Assignee
Mitsubishi Rayon Co Ltd
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 Mitsubishi Rayon Co Ltd filed Critical Mitsubishi Rayon Co Ltd
Priority to JP53081563A priority Critical patent/JPS5951340B2/en
Publication of JPS558844A publication Critical patent/JPS558844A/en
Publication of JPS5951340B2 publication Critical patent/JPS5951340B2/en
Expired legal-status Critical Current

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Description

【発明の詳細な説明】 本発明は、高温におけろ水処理や強放射性物質の化学的
分離、精製に適した粒子状無機イオン交換体の製造法に
関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing a particulate inorganic ion exchanger suitable for high-temperature effluent treatment and chemical separation and purification of strongly radioactive substances.

近年環境浄化の観点、又は資源の有効利用、特に地下資
源、海洋資源の有光利用の観点から砒素、クロム等の有
害物質を含む水の処理、又はウラン等の有価物質を含む
水からのこれら物質の濃縮、回収を効率よく行なうため
の技術の開発が行なわれている。
In recent years, from the perspective of environmental purification or the effective use of resources, especially the light use of underground resources and marine resources, the treatment of water containing harmful substances such as arsenic and chromium, or the treatment of water containing valuable substances such as uranium, has become increasingly important. Technologies are being developed to efficiently concentrate and recover substances.

上記の物質は通常水中においては砒酸イオン、亜砒酸イ
オン、クロム酸イオン、炭酸ウラニル、硫酸ウラニル等
のイオンとして存在しているため、イオン交換樹脂を使
用して処理、濃縮、回収等を行なうことが考えられる。
Since the above substances normally exist in water as ions such as arsenate ions, arsenite ions, chromate ions, uranyl carbonate, and uranyl sulfate, they can be treated, concentrated, and recovered using ion exchange resins. Conceivable.

しかしイオン交換樹脂はこれらイオンに対する選択性が
充分でなく、塩素イオン、臭素イオン等一価陰イオンが
多量に共存する系では上記イオンの交換容量が著しく低
下する。
However, ion exchange resins do not have sufficient selectivity for these ions, and in systems where large amounts of monovalent anions such as chloride ions and bromine ions coexist, the exchange capacity of the ions is significantly reduced.

更にイオン交換樹脂は高温下、強放射線下における安定
性に欠ける等の欠点も有している。
Furthermore, ion exchange resins also have drawbacks such as lack of stability under high temperatures and strong radiation.

一方無機イオン交換体はイオン交換樹脂に比較して高温
、強放射線下における安定性が優れており、さらに特殊
なイオンに対する選択的交換吸着能を有するものが多く
、高温下における水処理、強放射性物質の分離、濃縮、
精製等への応用が期待できる。
On the other hand, inorganic ion exchangers have superior stability at high temperatures and under strong radiation compared to ion exchange resins, and many also have selective exchange adsorption ability for special ions, so they can be used for water treatment at high temperatures and under strong radiation. separation and concentration of substances;
It can be expected to be applied to purification, etc.

一般に無機イオン交換体は充填塔方式で使用する場合に
は通液抵抗を減少させるために適当な大きさ、形態に成
形する必要がある、さらにこの成形体には、逆洗、再生
等の操作に充分耐えるだけの水中強度、耐酸性、耐アル
カリ性が要求される。
In general, when inorganic ion exchangers are used in a packed column system, it is necessary to mold them into an appropriate size and shape in order to reduce liquid flow resistance. It is required to have sufficient underwater strength, acid resistance, and alkali resistance.

無機イオン交換体の成形法としては、従来より無機の結
合剤として用いられているシリカゾル、水ガラス等を用
いて成形する方法が考えられる。
Possible methods for molding the inorganic ion exchanger include molding using silica sol, water glass, etc., which have been conventionally used as inorganic binders.

しかしかかる結合剤を用いて得られる成形体は耐アルカ
リ性が充分でなく、又成形前に比較してイオン交換能が
著るしく低下する。
However, the molded product obtained using such a binder does not have sufficient alkali resistance, and its ion exchange ability is significantly lower than that before molding.

さらに無機イオン交換体の成形法としては、セルロース
、合成・高分子等の有機系結合剤を用いて成形する方法
も考えられるが、有機系結合剤を用いた場合は成形体の
耐熱性及び耐酸、耐アルカリ性の点で不充分で高温下の
処理や強酸、強アルカリでの再生処理で成形体間の融着
や崩壊が起る。
Furthermore, as a method for molding inorganic ion exchangers, methods using organic binders such as cellulose and synthetic/polymer materials can also be considered, but when organic binders are used, the heat resistance and acid resistance of the molded product However, it is insufficient in alkali resistance, and fusion and collapse between molded bodies occur when treated at high temperatures or when recycled with strong acids or strong alkalis.

本発明者等は以上の如き状況を鑑み、イオン交換容量が
大きく、耐熱性、水中強度、耐酸性及び耐アルカリ性が
優れた粒子状の無機イオン交換体の製造法の開発に鋭意
検討した結果本発明を完成したものである。
In view of the above circumstances, the inventors of the present invention have conducted intensive studies to develop a method for producing a particulate inorganic ion exchanger that has a large ion exchange capacity and excellent heat resistance, underwater strength, acid resistance, and alkali resistance. It is a completed invention.

本発明の要旨とするところは、アナターゼ形もしくは無
定形の結晶構造を有するチタンの水和酸化物8モルに対
して無機酸0.1〜7.2モル及び水0〜50モルの割
合で混合し、混線、押し出し造粒した後乾燥することか
らなる粒子状無機イオン交換体の製造法にある。
The gist of the present invention is to mix 8 moles of a hydrated oxide of titanium having an anatase or amorphous crystal structure with an inorganic acid of 0.1 to 7.2 moles and water of 0 to 50 moles. However, there is a method for producing a particulate inorganic ion exchanger which comprises mixing, extrusion, granulation, and drying.

本発明に於いて用いるチタンの水和酸化物(以下チタン
酸と記す)トハ、TiO2・1]H20(n−0,5〜
20)の化学式で表わされるものであって且つアナター
ゼ形もしくは無定形の結晶構造を有するものである。
The hydrated oxide of titanium (hereinafter referred to as titanic acid) used in the present invention is TiO2.1]H20 (n-0,5~
20) and has an anatase or amorphous crystal structure.

このチタン酸は硫酸チタン又は四塩化チタンの水溶液を
加熱して加水分解するか、又はこれ等水溶液に塩基を加
えて中和することにより得られる固形分を水洗し、ろ別
後乾燥することにより得られる。
This titanic acid is obtained by heating and hydrolyzing an aqueous solution of titanium sulfate or titanium tetrachloride, or by adding a base to the aqueous solution to neutralize it, washing the solid content with water, filtering it, and then drying it. can get.

又このチタン酸は、チタンのテトラブトキシド、テl〜
ラインプロキシド等のアルコキトを水中で加水分解して
得られる固形分を水洗しろ別乾燥することによっても得
ることが出来る。
In addition, this titanic acid is titanium tetrabutoxide, tel~
It can also be obtained by hydrolyzing an alkoxyto such as line proxide in water, washing the solid content with water, and then drying it separately.

本発明に於いて用いられる無機酸としては、硫酸、塩酸
、燐酸等が挙げられる。
Inorganic acids used in the present invention include sulfuric acid, hydrochloric acid, phosphoric acid, and the like.

無機酸の添加量は、チタン酸8モルに対して0.1〜7
.2モルであるが、好ましくは硫酸(H2S04として
)の場合0.3〜3.0モル、塩酸(HClとして)の
場合1.2〜2.4モル、燐酸(H3PO4として)の
場合1.2〜3.6モルである。
The amount of inorganic acid added is 0.1 to 7 moles per 8 moles of titanic acid.
.. 2 moles, but preferably 0.3 to 3.0 moles for sulfuric acid (as H2S04), 1.2 to 2.4 moles for hydrochloric acid (as HCl), and 1.2 moles for phosphoric acid (as H3PO4). ~3.6 moles.

いずれも無機酸が0.1モル未満であると得られる粒子
状無機イオン交換体の水中における強度が著しく低下す
る。
In either case, when the amount of inorganic acid is less than 0.1 mol, the strength of the obtained particulate inorganic ion exchanger in water is significantly reduced.

又7.2モルを越えると混線時の混線物の粘度が著しく
上昇したり、又、固液が分離する現象が生じたりして押
し出し造粒は困難となるばかりでなく、硫酸、燐酸の場
合には焼成しても過剰の酸が表面に浸出し、さらに吸湿
して粒子表面かべとつく等の不都合が生ずる。
Moreover, if the amount exceeds 7.2 mol, the viscosity of the mixed material increases markedly, and a phenomenon of solid-liquid separation occurs, making extrusion granulation difficult. Even after firing, excessive acid leaches out to the surface and further absorbs moisture, causing problems such as the particle surface becoming sticky.

又、水の添加量はチタン酸8モルに対して0〜50モル
であるが、より好ましい添加量は押し出し造粒機の型式
やダイス、メツシュの孔径、押し出し速度、添加する無
機酸の量によって若干具なる。
The amount of water added is 0 to 50 moles per 8 moles of titanic acid, but the more preferable amount depends on the type of extrusion granulator, the pore size of the die and mesh, the extrusion speed, and the amount of inorganic acid added. It's a little rough.

例えば無機酸の添加量がチタン酸8モルに対して2モル
以下の場合、水を20〜50モル添加するのがより好ま
しい。
For example, when the amount of inorganic acid added is 2 moles or less per 8 moles of titanic acid, it is more preferable to add 20 to 50 moles of water.

混合、混線はバッチ式のものや連続式の捏和機を用いて
充分に行なう。
Mixing and cross-mixing should be thoroughly carried out using a batch type or continuous type kneading machine.

混線物は、スクリュー型押し出し造粒機、ロール型押し
出し造粒機、ブレード型押し出し造粒機等の造粒時に被
造粒物が加圧状態となる形式の造粒機を用いて造粒し粒
状物とする。
Mixed materials are granulated using a type of granulator that puts the granulated material under pressure during granulation, such as a screw type extrusion granulator, roll type extrusion granulator, or blade type extrusion granulator. Make it into granules.

押し出し造粒することによって、単に混練物を乾燥、焼
成したのより極めて強度の大きいイオン交換体を製造す
ることとができる。
By extrusion granulation, it is possible to produce an ion exchanger that is much stronger than that obtained by simply drying and calcining the kneaded material.

粒状物の粒径は造粒機のダイスもしくはスクリーンの孔
径を適当に選ふ゛ことによって一般的には0.3mmφ
以上の粒状物に造粒できる。
The particle size of the granules is generally 0.3 mmφ by appropriately selecting the hole diameter of the die or screen of the granulator.
It can be granulated into granules of the following types.

次いで粒状物を風乾あるいは加熱乾燥することにより本
発明のイオン交換体を得る。
Next, the ion exchanger of the present invention is obtained by air-drying or heat-drying the granules.

加熱乾燥を行なう場合は、加熱温度は500℃以下が好
ましい。
When heating and drying is performed, the heating temperature is preferably 500°C or lower.

加熱温度が500℃を越えると、得られるイオン交換体
のイオン交換容量が著しく低下する。
When the heating temperature exceeds 500°C, the ion exchange capacity of the resulting ion exchanger decreases significantly.

本発明の無機イオン交換体を充填塔に充填し、通水する
充填塔方式で使用する場合には、粒状のまま使用するか
、もしくは破砕整粒又は球形化して使用する。
When the inorganic ion exchanger of the present invention is packed in a packed tower and used in a packed tower system in which water is passed through it, it is used as it is in granular form, or after being crushed and sized or spheroidized.

本発明で得られる粒子状無機イオン交換体は耐熱性、耐
酸性、耐アルカリ性に優れ、水中強度も大きく交換容量
も大きくさらにイオン交換速度も充分大きい。
The particulate inorganic ion exchanger obtained by the present invention has excellent heat resistance, acid resistance, and alkali resistance, has high strength in water, has a large exchange capacity, and has a sufficiently high ion exchange rate.

更に本発明に於いては、用いる無機酸の種類によって得
られる粒子状無機イオン交換体のイオン交換能を大きく
変化させることが可能である。
Furthermore, in the present invention, the ion exchange ability of the particulate inorganic ion exchanger obtained can be greatly changed depending on the type of inorganic acid used.

すなわち硫酸及び塩酸を用いて製造したイオン交換体は
特に多価陰イオンの選択的交換吸着能に優れている。
That is, ion exchangers manufactured using sulfuric acid and hydrochloric acid are particularly excellent in selective exchange and adsorption ability for polyvalent anions.

これ等多価陰イオンの例としては、砒酸イオン、亜砒酸
イオン、クロム酸イオン、リン酸イオン、炭酸ウラニル
、硫酸ウラニル、モリブデン酸イオン、タングステン酸
イオン、バナジン酸イオン等が挙げられ、特に多量の塩
素イオン、臭素イオン等と共存する系に於けるこれら多
価陰イオンの除去、濃縮、回収に有効である。
Examples of these polyvalent anions include arsenate ion, arsenite ion, chromate ion, phosphate ion, uranyl carbonate, uranyl sulfate, molybdate ion, tungstate ion, vanadate ion, etc. It is effective in removing, concentrating, and recovering polyvalent anions in systems where chlorine ions, bromine ions, etc. coexist.

又燐酸を用いて製造した本発明のイオン交換体はセシウ
ム、ルビジウム、銀、カリウム、バリウム等のカチオン
の選択的交換能に優れており、これらカチオンの除去、
濃縮、回収に有効であり、又その選択性を利用してアル
カリ金属間の分離、アルカリ土類金属間の分離に使用す
ることが出来る。
In addition, the ion exchanger of the present invention produced using phosphoric acid has an excellent ability to selectively exchange cations such as cesium, rubidium, silver, potassium, and barium, and is capable of removing these cations.
It is effective for concentration and recovery, and its selectivity can be used to separate alkali metals and alkaline earth metals.

本発明で得られる無機イオン交換体は水中強度及び広範
囲のpH領域での安定性が優れている為1、通常のイオ
ン交換柑脂と同様に再生及び逆洗が可能である。
The inorganic ion exchanger obtained by the present invention has excellent strength in water and stability over a wide range of pH, 1 and can be regenerated and backwashed in the same way as ordinary ion-exchanged citrus.

再生剤としては塩酸、硫酸、水酸化ナトリウム、水酸化
カリウム、炭酸すトリウム、アンモニア水等を用いる。
As the regenerating agent, hydrochloric acid, sulfuric acid, sodium hydroxide, potassium hydroxide, sodium carbonate, aqueous ammonia, etc. are used.

本発明で得られる無機イオン交換体を用いて有害物質の
処理もしくは有価物質の濃縮、回収等を行なう方法とし
ては、有害物質もしくは有価物質を含有する水中に無機
イオン交換体を懸濁させた後ン濾過するいわゆるスラリ
一方式が゛用いられる。
A method for treating harmful substances or concentrating and recovering valuable substances using the inorganic ion exchanger obtained in the present invention includes suspending the inorganic ion exchanger in water containing harmful or valuable substances. A so-called slurry one-type method is used, which involves water filtering.

又無機イオン交換体を充填した充填塔に有害物質もしく
は有価物質の含有した水を通水する充填塔方式を用いる
ことも可能である。
It is also possible to use a packed tower system in which water containing harmful or valuable substances is passed through a packed tower filled with an inorganic ion exchanger.

本発明の無機イオン交換体は上記の如き特徴を利用して
地下水、地熱々水、鉱石処理廃水等に含まれる砒素の分
離除去、メッキ廃液からのクロムの回収等に用いること
が゛できる。
Utilizing the above characteristics, the inorganic ion exchanger of the present invention can be used for separating and removing arsenic contained in ground water, geothermal water, ore processing wastewater, and recovering chromium from plating waste liquid.

以下実施例により本発明を説明する。The present invention will be explained below with reference to Examples.

実施例 1 アナターゼ形のチタン酸(TiO(OH) 2 ) と
無機酸として硫酸、塩酸、燐酸各々と水を第1表の割合
で混合し、捏和機で充分混練した後、スクリュー型押し
出し造粒機で直径0.5mmφのスクリーンを通すこと
により、長さ3〜7mm、粒径0,5mmφの成形物を
得た。
Example 1 Anatase titanic acid (TiO(OH) 2 ), sulfuric acid, hydrochloric acid, phosphoric acid as an inorganic acid, and water were mixed in the proportions shown in Table 1, thoroughly kneaded with a kneader, and then extruded into a screw type. By passing through a screen with a diameter of 0.5 mm in a granulator, molded products with a length of 3 to 7 mm and a particle size of 0.5 mm were obtained.

次いでこの成形物を110℃の温風中で16時間乾燥し
た後、300℃で3時間型湯気炉中で焼成するこにより
粒子状無機イオン交換体を得た。
Next, this molded product was dried in hot air at 110°C for 16 hours, and then fired in a steam furnace at 300°C for 3 hours to obtain a particulate inorganic ion exchanger.

得られたイオン交換体の強度を判定する為に300cc
ビーカーに90℃の熱水を300cc入れ、それに上記
のイオン交換体10.0gを粉をよくふるって漫潰し、
ジャーテスターでファンの回転150r、p、m。
300cc to judge the strength of the obtained ion exchanger.
Pour 300 cc of 90°C hot water into a beaker, add 10.0 g of the above ion exchanger to it, sift the powder thoroughly, and mash.
Fan rotation 150r, p, m with jar tester.

にし5時間攪拌処理する。Stir for 5 hours.

のちイオン交換体をろ別し電気炉中で300℃で3時間
焼成し48メツシユのふるいでふるい、48メツシユの
ふるいを通過する粉の割合を粒分率として第1表に示し
た。
Thereafter, the ion exchanger was filtered out, calcined in an electric furnace at 300° C. for 3 hours, and sieved through a 48-mesh sieve, and the proportion of powder passing through the 48-mesh sieve is shown in Table 1 as the particle fraction.

又同じイオン交換体の耐酸、耐アルリ性の評価を行うた
めに25%の水酸化すトリウム水溶液及び濃硫酸各々5
0ccにイオン交換体1.0gを浸漬し、ときどきふり
まぜながら24時間放置後、形態の変化を観察した結果
を第1表に示す。
In addition, in order to evaluate the acid resistance and alkaline resistance of the same ion exchanger, 5% each of 25% thorium hydroxide aqueous solution and concentrated sulfuric acid was used.
Table 1 shows the results of observing changes in morphology after immersing 1.0 g of ion exchanger in 0 cc and leaving it for 24 hours with occasional shaking.

又比較の為上記チタン酸にシリカゲル(水分率80%)
及びケイ酸すl〜リウム水溶液(水分率68%)を第1
表に示す通りに加え、上記と同様の方法で成形して得ら
れた成形物について同様の評価を行なった結果も第1表
に示す。
For comparison, silica gel (80% moisture content) was added to the titanic acid mentioned above.
and sulfur to lithium silicate aqueous solution (moisture content 68%) as the first
In addition to the results shown in the table, Table 1 also shows the results of similar evaluations of molded products obtained by molding in the same manner as above.

実施例 2 無定形チタン酸、硫酸及び水を第2表の割合で用い、実
施例1と同様な方法で粒径1mmφに押し出し成形、乾
燥、焼成を行ない、得られた成形物を用い実施例1と同
一条件で求めた熱水中強度(粒分率)を第2表に示した
Example 2 Using amorphous titanic acid, sulfuric acid, and water in the proportions shown in Table 2, extrusion molding to a particle size of 1 mmφ was carried out in the same manner as in Example 1, drying, and firing, and the obtained molded product was used to conduct an example. Table 2 shows the strength in hot water (particle fraction) determined under the same conditions as in Example 1.

別に試料ビンに砒素として1100ppの砒酸水溶液1
00m1をとり、これに上記の成形物1.Ogを添加し
、攪拌しながら40℃で3時間処理した。
Separately, put 1100pp arsenic acid aqueous solution 1 as arsenic in a sample bottle.
Take 00ml and add the above molded product 1. Og was added and treated at 40° C. for 3 hours with stirring.

この結果得られた砒素残存量を第2表に示す。The residual amounts of arsenic obtained as a result are shown in Table 2.

比較例 1 実施例2で用い無定形チタン酸粉末の砒素吸着能を実施
例2と同一条件で測定した。
Comparative Example 1 The arsenic adsorption ability of the amorphous titanic acid powder used in Example 2 was measured under the same conditions as in Example 2.

その結果砒素残存度は40p狸であり、本発明で得られ
る粒状無機イオン交換体に比較して砒素吸着能がかなり
劣る。
As a result, the arsenic residual degree was 40p, and the arsenic adsorption ability was considerably inferior to that of the granular inorganic ion exchanger obtained by the present invention.

実施例 3 実施例1と同様の方法で、アナターゼ形チタン酸800
gに対し濃硫酸67cc及び水400ccを添加し成形
した成形物の乾燥及焼成条件を変えたものについて、実
施例2と同様に水中強度の評価及び砒素処理を評価した
結果を第3表に示した。
Example 3 In the same manner as in Example 1, anatase titanic acid 800
Table 3 shows the results of evaluating the strength in water and the arsenic treatment in the same manner as in Example 2 for molded products made by adding 67 cc of concentrated sulfuric acid and 400 cc of water to the molded product, and changing the drying and firing conditions. Ta.

Claims (1)

【特許請求の範囲】[Claims] 1 アナターゼ形もしくは無定形の結晶構造を有するチ
タンの水和酸化物8モルに対して無機酸0.1〜7.2
モル級び水0〜50モルの割合で混合し、混練、押し出
し造粒した後乾燥することを特徴とする粒子状無機イオ
ン交換体の製造法。
1 0.1 to 7.2 inorganic acid per 8 moles of hydrated titanium oxide having anatase or amorphous crystal structure
1. A method for producing a particulate inorganic ion exchanger, which comprises mixing 0 to 50 moles of water, kneading, extruding, granulating, and drying.
JP53081563A 1978-07-05 1978-07-05 Method for producing particulate inorganic ion exchanger Expired JPS5951340B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53081563A JPS5951340B2 (en) 1978-07-05 1978-07-05 Method for producing particulate inorganic ion exchanger

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53081563A JPS5951340B2 (en) 1978-07-05 1978-07-05 Method for producing particulate inorganic ion exchanger

Publications (2)

Publication Number Publication Date
JPS558844A JPS558844A (en) 1980-01-22
JPS5951340B2 true JPS5951340B2 (en) 1984-12-13

Family

ID=13749754

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53081563A Expired JPS5951340B2 (en) 1978-07-05 1978-07-05 Method for producing particulate inorganic ion exchanger

Country Status (1)

Country Link
JP (1) JPS5951340B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0257510U (en) * 1988-10-19 1990-04-25

Also Published As

Publication number Publication date
JPS558844A (en) 1980-01-22

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