JPH0212637B2 - - Google Patents
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- Publication number
- JPH0212637B2 JPH0212637B2 JP10290883A JP10290883A JPH0212637B2 JP H0212637 B2 JPH0212637 B2 JP H0212637B2 JP 10290883 A JP10290883 A JP 10290883A JP 10290883 A JP10290883 A JP 10290883A JP H0212637 B2 JPH0212637 B2 JP H0212637B2
- Authority
- JP
- Japan
- Prior art keywords
- pickling
- tank
- acid
- liquid
- present
- 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
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C23—COATING METALLIC MATERIAL; COATING MATERIAL WITH METALLIC MATERIAL; CHEMICAL SURFACE TREATMENT; DIFFUSION TREATMENT OF METALLIC MATERIAL; COATING BY VACUUM EVAPORATION, BY SPUTTERING, BY ION IMPLANTATION OR BY CHEMICAL VAPOUR DEPOSITION, IN GENERAL; INHIBITING CORROSION OF METALLIC MATERIAL OR INCRUSTATION IN GENERAL
- C23G—CLEANING OR DE-GREASING OF METALLIC MATERIAL BY CHEMICAL METHODS OTHER THAN ELECTROLYSIS
- C23G1/00—Cleaning or pickling metallic material with solutions or molten salts
- C23G1/36—Regeneration of waste pickling liquors
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Removal Of Specific Substances (AREA)
- Cleaning And De-Greasing Of Metallic Materials By Chemical Methods (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Description
【発明の詳細な説明】
本発明は金属を酸洗する酸洗液の処理方法に関
する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating a pickling solution for pickling metals.
従来、鉄材又は鉄合金よりなる板、鋼板などの
金属にメツキや塗装、その他の表面処理を施す場
合、これらの処理に先立つて錆除去などの目的で
酸洗が行われることは周知である。かかる酸洗に
用いられる溶液としては、例えば塩酸、硫酸など
の鉱酸水溶液であり、金属の酸洗によつて生じた
廃液は、なお多量の酸を含有している。これを廃
棄すれば、酸の損失であるばかりか、公害を招く
おそれがあるため、一般に中和を行うが費用が嵩
む。そこで近年、これらの酸洗廃液から酸を回収
し、再使用する試みがなされ、特に陰イオン交換
膜を用いた拡散透析を組合せた金属酸洗システム
が提案されている。かかるシステムによれば、酸
洗槽内液の一部を拡散透析に付して酸を回収再使
用すると同時にその被処理液は場合によつて更に
別工程において鉄化合物などを回収した後に廃棄
される。このようなシステムなどの方法で酸の有
効利用を図ることにより、酸の実質的な消費量は
従来の方法に比べ著しく減少する。しかしなが
ら、別の問題として酸洗に伴い金属や、使用薬剤
から不可避的に持ち込まれる種々の不純物が酸洗
液中に蓄積されることが判つた。 BACKGROUND ART Conventionally, it is well known that when plating, painting, or other surface treatments are applied to metals such as iron or iron alloy plates, steel plates, etc., pickling is performed for the purpose of removing rust or the like prior to these treatments. The solution used for such pickling is, for example, an aqueous mineral acid solution such as hydrochloric acid or sulfuric acid, and the waste liquid produced by pickling the metal still contains a large amount of acid. If this is disposed of, not only will there be a loss of acid, but there is also the risk of causing pollution, so neutralization is generally carried out, but this is expensive. Therefore, in recent years, attempts have been made to recover and reuse acid from these pickling waste liquids, and in particular, a metal pickling system that combines diffusion dialysis using an anion exchange membrane has been proposed. According to such a system, a part of the solution in the pickling tank is subjected to diffusion dialysis to recover and reuse the acid, and at the same time, the treated solution is disposed of after recovering iron compounds and the like in a separate process depending on the case. Ru. By making effective use of acid in methods such as this system, the actual amount of acid consumed is significantly reduced compared to conventional methods. However, it has been found that another problem is that metals and various impurities inevitably introduced from the chemicals used accumulate in the pickling solution.
特に酸洗液中の銅イオンがある濃度以上に蓄積
すると、これが鉄などの金属表面に析出付着し、
次工程での表面処理などに悪影響をおよぼすため
SS分と共に除去しなければならない。本発明者
等は上記の銅イオンの除去方法について特願昭57
−84916号及び特願昭58−33804号の発明を提案し
た。即ち、これらの方法によれば、酸洗槽より酸
洗液を抜き出し、再供給する循環液に可溶性硫黄
化合物を添加することにより、脱銅効果が極めて
良好である。ところが、SS分の除去のために用
いられる凝集剤と上記の可溶性硫黄化合物を併用
して凝集・濾過する場合、脱銅効果とSS分の除
去効果の両方を同時に満足させることが困難であ
つた。 In particular, when copper ions in the pickling solution accumulate above a certain concentration, they precipitate and adhere to the surface of metals such as iron.
This may adversely affect surface treatment in the next process.
It must be removed along with the SS portion. The inventors of the present invention filed a patent application in 1982 regarding the method for removing copper ions mentioned above.
-84916 and Japanese Patent Application No. 58-33804. That is, according to these methods, the pickling liquid is extracted from the pickling tank and a soluble sulfur compound is added to the circulating liquid to be resupplied, thereby achieving an extremely good decopper removal effect. However, when coagulating and filtering using a flocculant used to remove SS components and the above-mentioned soluble sulfur compounds, it was difficult to simultaneously satisfy both the copper removal effect and the SS removal effect. .
本発明者は、上記原因について検討した結果、
凝集剤と可溶性硫黄化合物を併用する場合には、
処理液の温度が極めて重要であるという知見を得
て本発明を完成するに至つた。 As a result of studying the above causes, the inventor found that
When using coagulants and soluble sulfur compounds,
The present invention was completed based on the knowledge that the temperature of the processing liquid is extremely important.
即ち、本発明は、金属の酸洗槽より抜き出され
た酸洗液(即ち、酸洗廃液)を、20〜50℃に保持
しつつ凝集剤及び銅イオンと不溶性化合物を形成
し得る可溶性硫黄化合物を添加して、沈殿物を分
離した後、少なくとも一部の分離液を酸の除去を
行うことなく、酸洗槽に再供給することを特徴と
する酸洗液の処理方法である。従つて、本発明に
よれば酸洗槽へ循環再供給される酸洗液は銅イオ
ンが除去された酸液となつて酸洗槽に再供給され
るため、酸洗槽中の酸洗液は、常にほぼ一定の金
属の洗浄に支障のない低い銅イオン濃度に保つこ
とが可能となる。 That is, the present invention maintains the pickling liquid (i.e., pickling waste liquid) extracted from a metal pickling tank at a temperature of 20 to 50°C, and absorbs soluble sulfur that can form an insoluble compound with a flocculant and copper ions. This method of treating a pickling liquid is characterized in that, after adding a compound and separating a precipitate, at least a portion of the separated liquid is re-supplied to a pickling tank without removing the acid. Therefore, according to the present invention, the pickling liquid that is circulated and re-supplied to the pickling tank becomes an acid solution from which copper ions have been removed and is re-supplied to the pickling tank. This makes it possible to always maintain a low copper ion concentration that does not interfere with metal cleaning.
本発明は、また酸洗廃液に特定な添加剤を添加
し、凝集・濾過するに際して該酸洗廃液の温度を
20〜50℃、好ましくは30〜40℃にすることが重要
で該温度にすることにより、酸洗廃液中のSS分
及び銅イオンを効率よく除去でき、しかも濾過効
率を上昇させることが出来る。酸洗廃液の温度が
50℃より高い場合には、可溶性硫黄化合物と銅の
反応によつて生じた不溶性塩が分解し再溶解する
ため、脱銅効果が劣る。また、20℃より低い温度
では濾過効率が低下するため、本発明の目的を達
成することは出来ない。上記温度にコントロール
する方法は、例えば燃交換器を用いる方法など、
特に制限されるものではない。 The present invention also adds specific additives to the pickling waste liquid, and controls the temperature of the pickling waste liquid during coagulation and filtration.
It is important to keep the temperature at 20 to 50°C, preferably 30 to 40°C.By setting the temperature to this temperature, the SS content and copper ions in the pickling waste liquid can be efficiently removed, and the filtration efficiency can be increased. The temperature of pickling waste liquid is
If the temperature is higher than 50°C, the insoluble salt produced by the reaction between the soluble sulfur compound and copper is decomposed and redissolved, resulting in a poor copper removal effect. Furthermore, at temperatures lower than 20°C, the filtration efficiency decreases, making it impossible to achieve the object of the present invention. Methods of controlling the temperature above include, for example, using a fuel exchanger.
There are no particular restrictions.
本発明に用いられる凝集剤としては、例えば高
分子凝集剤の如く酸洗廃液中のSS分を凝集させ
る効果が大きいものが好ましく用いられるが、特
に制限されるものでなく、公知のものが使用出来
る。また、本発明に用いられる凝集剤は、上記効
果を増加させる目的の他の凝集剤を併用すること
も制限されるものでなく、特にケイソウ土等の濾
過助剤を併用することにより、本発明の効果は顕
著になる。 The flocculant used in the present invention is preferably one that has a large effect of flocculating the SS content in the pickling waste liquid, such as a polymer flocculant, but is not particularly limited, and known agents can be used. I can do it. Further, the flocculant used in the present invention is not limited to the use of other flocculants for the purpose of increasing the above-mentioned effects, and in particular, the flocculant used in the present invention can be used in combination with a filter aid such as diatomaceous earth. The effect becomes noticeable.
本発明に用いられる可溶性硫黄化合物として
は、硫化ソーダ、水硫化ソーダ、多硫化ソーダ等
のアルカリ金属の硫黄化合物の如く銅と不溶性塩
を形成する物質、或いはチオ尿素及びエチルチオ
尿素、ジエチルチオ尿素、ブチルチオ尿素、フエ
ニルチオ尿素等のチオ尿素誘導体、又は重金属除
去剤として一般的に使用されている含硫黄又はチ
オ尿素系除去剤例えば(商品名:オリトール(オ
リエンタル技研製)、インヒビター:イビツトS
600、(朝日化学工業製)etc)の如く銅イオン
と錯体を形成して沈澱する物質等がある。中でも
チオ尿素及びその誘導体を用いたものは本発明の
効果が極めて大きいことから好ましい。 The soluble sulfur compounds used in the present invention include substances that form insoluble salts with copper, such as sulfur compounds of alkali metals such as sodium sulfide, sodium hydrogen sulfide, and sodium polysulfide, or thiourea, ethylthiourea, diethylthiourea, and butylthiourea. Thiourea derivatives such as urea and phenylthiourea, or sulfur-containing or thiourea-based removers commonly used as heavy metal removers, such as (trade name: Oritol (manufactured by Oriental Giken), inhibitor: Ivit S
There are substances that form complexes with copper ions and precipitate, such as 600 (manufactured by Asahi Chemical Industries), etc. Among these, those using thiourea and its derivatives are preferred because the effects of the present invention are extremely large.
上記に示した凝集剤及び可溶性硫黄化合物の添
加量は酸洗廃液中のSS分及び銅イオン濃度によ
り適宜選定されるが、一般には凝集剤50〜
200ppm、可溶性硫黄化合物100〜500ppmが用い
られる。 The amounts of the flocculant and soluble sulfur compound shown above are appropriately selected depending on the SS content and copper ion concentration in the pickling waste solution, but generally the flocculant is 50~
200 ppm and 100-500 ppm of soluble sulfur compounds are used.
この際、該酸洗廃液は凝集を容易にし、且つ凝
集物の再溶解を防止するため還元雰囲気にするこ
とが好ましい。 At this time, the pickling waste liquid is preferably kept in a reducing atmosphere in order to facilitate agglomeration and prevent re-dissolution of aggregates.
本発明の濾過のために用いられる方法、装置等
については例えばフイルタープレスによる方法
等、特に制限されるものではない。 The method, device, etc. used for the filtration of the present invention are not particularly limited, and may include, for example, a method using a filter press.
以下、本発明の処理方法を用いた代表的1例を
図面に基づき詳細に説明する。第1図は、本発明
方法を用いた処理システムを示す工程図である。
図中1が酸洗槽であり、一般に塩酸又は硫酸等の
鉱酸の1〜10規定、好ましくは4〜8規定水溶液
であり、酸洗時に一部金属と反応して生ずる、例
えば塩化鉄、硫酸鉄などを数重量%含んだ酸洗液
が存在しており、これに被処理金属を浸漬するか
或いは上記酸洗液のシヤワーに金属を曝露するな
どの公知の洗浄方式により処理される。本発明に
あつては、該酸洗槽内の酸洗廃液の少なくとも一
部をパイプ11を通して抜き出し、必要により静
定し、場合によつては一部をパイプ21によりバ
イパスして酸洗槽へ戻すと共に残部を熱交換器2
に送入し、温度を20〜50℃に調節して、凝集・濾
過槽3に送入し、該槽で所定量の凝集剤及び可溶
性硫黄化合物を添加し、凝集・濾過させる。 Hereinafter, a typical example using the processing method of the present invention will be explained in detail based on the drawings. FIG. 1 is a process diagram showing a processing system using the method of the present invention.
In the figure, 1 is a pickling tank, which is generally a 1 to 10 N, preferably 4 to 8 N aqueous solution of a mineral acid such as hydrochloric acid or sulfuric acid. There is a pickling solution containing several weight percent of iron sulfate, etc., and the metal to be treated is treated by a known cleaning method such as immersing the metal in this or exposing the metal to a shower of the pickling solution. In the present invention, at least a portion of the pickling waste liquid in the pickling tank is extracted through the pipe 11, allowed to settle if necessary, and in some cases, a portion is bypassed through the pipe 21 and sent to the pickling tank. Return it and transfer the remainder to heat exchanger 2.
The temperature is adjusted to 20 to 50°C, and the mixture is sent to a flocculation/filtration tank 3, where predetermined amounts of flocculant and soluble sulfur compound are added, and flocculation/filtration is performed.
上記凝集・濾過槽の構造は、特に制限されな
い。一般に可溶性硫黄化合物及び凝集剤の添加
は、酸洗槽から抜き出しラインのうち、凝集・濾
過槽以前であればどこでもよいが熱交換器以後の
ラインで連続又は間歇的に添加しつつ凝集・濾過
させるのがよい。凝集・濾過槽に供給された酸洗
廃液は固液分離され、濾過液(酸)はパイプ13
及び14の経路により酸洗槽に再供給する。 The structure of the aggregation/filtration tank is not particularly limited. Generally, soluble sulfur compounds and flocculants can be added anywhere in the extraction line from the pickling tank before the flocculation/filtration tank, but they are added continuously or intermittently in the line after the heat exchanger for flocculation/filtration. It is better. The pickling waste liquid supplied to the coagulation/filtration tank is separated into solid and liquid, and the filtrate (acid) is passed through pipe 13.
and 14 routes to re-supply the pickling tank.
更に本発明においては、パイプ12以後におい
て、過液(分離液)を分割し、その一方は直接
(即ち、付加的な処理を施すことなく)パイプ1
3及び14の経路により酸洗槽に再供給すると共
に、他方の少なくとも一部は、パイプ15より拡
散透析装置4により処理することも好ましい。該
装置は、一般に知られている拡散透析装置であ
り、透析膜として陰イオン交換膜が用いられる。 Furthermore, in the present invention, the filtrate (separated liquid) is divided after the pipe 12, and one of the filtrate is directly (i.e., without any additional treatment) into the pipe 1.
It is also preferable that the pickling tank is resupplied through routes 3 and 14, and that at least a portion of the other one is treated by the diffusion dialysis device 4 through the pipe 15. This device is a generally known diffusion dialysis device, and an anion exchange membrane is used as the dialysis membrane.
該拡散透析装置において、一方に水を供給し、
これに酸を回収してパイプ16よりタンク5に至
る。他方、酸を除かれた液は、17より系外に排
出される。これは必要により金属成分の回収処理
などを行つた後、廃棄される。タンク5において
は、酸洗の状態に応じて追加の酸の添加、水の補
給あるいは他の薬剤の添加を行い、パイプ18よ
りパイプ14を経由するか又は経由せずに酸洗槽
に再供給される。 In the diffusion dialysis device, water is supplied to one side,
The acid is recovered and delivered to the tank 5 through a pipe 16. On the other hand, the liquid from which the acid has been removed is discharged from the system through 17. This is disposed of after performing recovery processing for metal components as necessary. In the tank 5, additional acid is added, water is replenished, or other chemicals are added depending on the pickling condition, and the water is re-supplied from the pipe 18 to the pickling tank via the pipe 14 or not. be done.
本発明において循環する酸洗液の量は、そのプ
ロセスによつて異なるが、一般に酸洗槽内の攪拌
状態を良好にする目的、或いは槽内酸濃度を所定
の範囲内に維持する目的、更には槽内に不可避的
に持ち込まれる不純物の濃度を一定限度以下に維
持する目的など必要とする目的に適合する量を選
定すればよい。 The amount of pickling solution circulated in the present invention varies depending on the process, but generally the purpose is to improve the stirring state in the pickling tank, or to maintain the acid concentration in the tank within a predetermined range, and The amount may be selected to suit the desired purpose, such as maintaining the concentration of impurities unavoidably brought into the tank below a certain limit.
また循環液の少なくとも一部を拡散透析処理に
付する場合の拡散透析装置への供給量は、酸洗槽
内で副生する鉄などの金属の塩を一定濃度以下に
保持し得る量、換言すれば該槽での金属塩の単位
時間当りの副生量を除去するに足る液量を拡散透
析装置に供給、処理すればよい。 In addition, when at least a part of the circulating fluid is subjected to diffusion dialysis treatment, the amount supplied to the diffusion dialysis device is the amount that can keep the salts of metals such as iron produced as by-products in the pickling tank below a certain concentration. In this case, an amount of liquid sufficient to remove the amount of by-product of the metal salt per unit time in the tank may be supplied to the diffusion dialysis apparatus and processed.
以下、本発明詳細に説明するために実施例を示
すが、本発明は以下の実施例に特に限定されるも
のではない。 EXAMPLES Hereinafter, examples will be shown to explain the present invention in detail, but the present invention is not particularly limited to the following examples.
実施例 1
塩酸145.8g/、Fe53.1g/、Cu333ppm、
SS325ppmを含む酸洗廃液を34℃に維持して高分
子凝集剤ハイモロツクK−380(協立有機製)を
100ppm添加し、5分間凝集反応させた。次にチ
オ尿素5%水溶液を300ppm処理し、10分間反応
させた。これにケイソウ土200ppmを今後して50
cmフイルタープレステスト機にて濾過した。Example 1 Hydrochloric acid 145.8g/, Fe53.1g/, Cu333ppm,
The pickling waste liquid containing SS325ppm was maintained at 34℃ and the polymer flocculant Himoroku K-380 (manufactured by Kyoritsu Organic Co., Ltd.) was applied.
100 ppm was added and the agglutination reaction was carried out for 5 minutes. Next, 300 ppm of 5% thiourea aqueous solution was treated and reacted for 10 minutes. Add 200ppm of diatomaceous earth to this and add 50
Filtered using cm filter press test machine.
結果は次の通りであつた。 The results were as follows.
処理能力:2.6/Hr
処理液Cu:155ppm
比較例 1
塩酸145.8g/、Fe53.1g/、Cu333ppm、
SS925ppmを含む酸洗廃液を55℃に維持して高分
子凝集剤ハイモロツクK−380(協立有機製)を
100ppm添加し、5分間凝集反応させた。次にチ
オ尿素5%水溶液を300ppm添加し、10分間反応
させた。これにケイソウ土200ppmを混合して50
cmフイルタープレステスト機にて濾過した。Processing capacity: 2.6/Hr Processing liquid Cu: 155ppm Comparative example 1 Hydrochloric acid 145.8g/, Fe53.1g/, Cu333ppm,
The pickling waste solution containing SS925ppm was maintained at 55℃ and the polymer flocculant Himoroku K-380 (manufactured by Kyoritsu Organic Co., Ltd.) was applied.
100 ppm was added and the agglutination reaction was carried out for 5 minutes. Next, 300 ppm of 5% thiourea aqueous solution was added and reacted for 10 minutes. Mix 200ppm of diatomaceous earth with this and make 50
Filtered using cm filter press test machine.
結果は次の通りであつた。 The results were as follows.
処理能力:3.7/Hr
処理液Cu:189ppm
比較例 2
比較例1と同じ酸洗廃液を17℃に維持して高分
子凝集剤ハイモロツクK−380(協立有機製)を
100ppm添加し、5分間凝集反応させた。次にチ
オ尿素5%水溶液を300ppm添加し、10分間反応
させた。これにケイソウ土200ppmを混合して50
cmフイルタープレステスト機にて濾過した。Processing capacity: 3.7/Hr Processing liquid Cu: 189ppm Comparative example 2 The same pickling waste liquid as in Comparative example 1 was maintained at 17°C and the polymer flocculant Himorok K-380 (manufactured by Kyoritsu Organic Co., Ltd.) was added.
100 ppm was added and the agglutination reaction was carried out for 5 minutes. Next, 300 ppm of 5% thiourea aqueous solution was added and reacted for 10 minutes. Mix 200ppm of diatomaceous earth with this and make 50
Filtered using cm filter press test machine.
結果は次の通りであつた。 The results were as follows.
処理能力:1.2/Hr 処理液Cu:126ppmProcessing capacity: 1.2/Hr Processing liquid Cu: 126ppm
第1図は本発明方法を用いた処理システムを示
す工程図ある。図において1は酸洗槽、2は熱交
換器、3は凝集・濾過槽、4は拡散透析装置、5
はタンクである。
FIG. 1 is a process diagram showing a processing system using the method of the present invention. In the figure, 1 is a pickling tank, 2 is a heat exchanger, 3 is a coagulation/filtration tank, 4 is a diffusion dialysis device, and 5
is a tank.
Claims (1)
〜50℃に保持しつつ凝集剤及び銅イオンと不溶性
化合物を形成し得る可溶性硫黄化合物を添加し
て、沈殿物を分離した後少なくとも一部の分離液
を酸の除去を行うことなく酸洗槽に再供給するこ
とを特徴とする酸洗液の処理方法。1. The pickling liquid extracted from the metal pickling tank is
After separating the precipitate by adding a flocculant and a soluble sulfur compound that can form an insoluble compound with copper ions while maintaining the temperature at ~50°C, at least a portion of the separated liquid is transferred to a pickling tank without removing the acid. A method for treating a pickling solution, characterized in that the pickling solution is resupplied.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10290883A JPS59228992A (en) | 1983-06-10 | 1983-06-10 | Treatment of pickling waste liquid |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP10290883A JPS59228992A (en) | 1983-06-10 | 1983-06-10 | Treatment of pickling waste liquid |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS59228992A JPS59228992A (en) | 1984-12-22 |
| JPH0212637B2 true JPH0212637B2 (en) | 1990-03-22 |
Family
ID=14339953
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP10290883A Granted JPS59228992A (en) | 1983-06-10 | 1983-06-10 | Treatment of pickling waste liquid |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS59228992A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105236605A (en) * | 2015-10-29 | 2016-01-13 | 佛山市顺德区美的饮水机制造有限公司 | Compound filter element and water purifier provided with same |
-
1983
- 1983-06-10 JP JP10290883A patent/JPS59228992A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS59228992A (en) | 1984-12-22 |
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