JPH04304327A - Treatment of decopperized dross - Google Patents

Treatment of decopperized dross

Info

Publication number
JPH04304327A
JPH04304327A JP3089371A JP8937191A JPH04304327A JP H04304327 A JPH04304327 A JP H04304327A JP 3089371 A JP3089371 A JP 3089371A JP 8937191 A JP8937191 A JP 8937191A JP H04304327 A JPH04304327 A JP H04304327A
Authority
JP
Japan
Prior art keywords
tin
dross
copper
leaching
aluminum
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.)
Granted
Application number
JP3089371A
Other languages
Japanese (ja)
Other versions
JP3060574B2 (en
Inventor
Akira Yoshioka
明 吉岡
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 Materials Corp
Original Assignee
Mitsubishi Materials Corp
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 Materials Corp filed Critical Mitsubishi Materials Corp
Priority to JP8937191A priority Critical patent/JP3060574B2/en
Publication of JPH04304327A publication Critical patent/JPH04304327A/en
Application granted granted Critical
Publication of JP3060574B2 publication Critical patent/JP3060574B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

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  • Manufacture And Refinement Of Metals (AREA)

Abstract

PURPOSE:To easily recover tin in a high yield by treating a decopperized dross with a hydrochloric acid, selectively leaching tin, separating the leaching solution, dipping aluminum pieces into this solution and precipitating metallic tin. CONSTITUTION:The decopperized dross containing of metallic tin and copper as main components is dipped into the conc. hydrochloric acid at a room temp. By this method, the metallic tin in the decopperized dross is selectively leached as SnCl2. Successively, the leaching solution and leaching slag are separated by filtration, etc. Thereafter, the aluminum pieces are dipped into the leaching solution and the metallic tin is precipitated and recovered as crude tin. On the other hand, in the leaching slag, copper is concentrated and used as raw material in a copper refining. Further, in the condition of incorporating scrap containing the aluminum in a flexible bag 2 having water permeability composed of acid resistance synthetic resin fiber, etc., this is dipped and washed in a cementation tank 1, water washing tank 5 and compressive squeezing machine 6 successively through a beam 3 and a lifting machine 4, and after removing the water, by carrying out by a container 7, recovery of the tin and the aluminum scrap can be efficiently treated.

Description

【発明の詳細な説明】 【0001】 【産業上の利用分野】本発明は脱銅ドロス処理法に関す
るものである。更に詳しくは錫精錬工程中に発生する金
属錫と硫化銅を主成分とする脱銅ドロスを処理し錫を回
収する脱銅ドロス処理法に関するものである。 【0002】 【従来の技術】脱銅ドロスは錫精錬工程中に、粗錫中に
含有されていた銅を硫黄を加えて硫化銅として除去した
際に生じたものである。銅の除去に際し錫が大量に脱銅
ドロス中に混入している。R.A.WRIGHT著、「
Extractive  Metallurgyof 
 Tin」、2nd  Ed.,ELSEVIER出版
社、1982年、p226には酸化ばい焼法による脱銅
ドロスの後処理が記載されている。 【0003】 【発明が解決しようとする課題】しかし、近年良質の錫
原料が減少し、又資源の有効利用の観点から良質でない
錫原料の使用が増え、それに伴って脱銅ドロスの発生量
が増大しているため有効な利用が必要になってきた。脱
銅ドロスの後処理は困難であって、前記酸化ばい焼法は
ばい焼中に銅−錫合金が生成して焼結する傾向が強く、
後処理の容易なばい焼が困難で、適当な処理方法ではな
かった。その他の適当な処理方法もなく有効に利用され
ていなかった。一方回収錫原料の中にアルミニウム片を
大量に含有するスクラップが多くなってきて、これを脱
銅ドロスと共に容易に処理することが要求されている。 【0004】本発明は上記課題に鑑み、ドロスを処理し
て容易に錫を回収し、併せてアルミニウム片を含有する
スクラップを処理する方法を提供することを目的とする
。 【0005】 【課題を解決するための手段】本発明において、金属錫
と硫化銅を主成分とする脱銅ドロスを塩酸により処理し
て錫を選択的に浸出し、浸出液と浸出滓とを分離した後
、浸出液中にアルミニウム片を浸漬して錫を回収する脱
銅ドロス処理法を構成した。併せて該浸出液中の浸漬及
び引き続く水洗並びに脱水の一連の工程を、該アルミニ
ウム片を含有するスクラップを良好な水透過性及び可撓
性を有する容器中に入れたままの状態で行う脱銅ドロス
処理法を構成した。 【0006】 【作用】金属錫と硫化銅を主成分とする脱銅ドロスを常
温において濃塩酸中に浸漬すると、金属錫が水素を発生
し溶解して脱銅ドロスはスラリーとなる。濾過等の常法
により固液分離すると浸出液中に錫が脱銅ドロスより9
0パーセント以上溶出し、塩化錫SnCl2 溶液とな
る。浸出液中にアルミニウム片を浸漬すると金属錫が析
出し、粗錫として利用される。この時アルミニウム片を
含有するスクラップは良好な水透過性及び可撓性を有す
る容器中に入れたままの状態で、一連の浸漬、水洗、脱
水の工程にかけられるのが好ましい。尚、浸出滓は銅が
60パーセント以上に濃縮され、錫は数パーセントに過
ぎないから、銅精錬の原料となる。 【0007】 【実施例】本発明の一実施例を図1により説明する。図
1は脱銅ドロスの一連の処理装置を示す図である。脱銅
ドロス1tを特に粉砕することなく、常温において耐酸
タンク中の2m3 の濃塩酸中に攪拌しながら少量ずつ
投入した。過度に反応が激しくならないように水素の発
生状況を見ながら投入する。この際水素と共に硫化水素
が発生するから局所排気をし、又水素濃度が爆発濃度に
ならないように留意する。1t全部を投入するのに約2
時間かかり終了した。その後も攪拌を続け10時間浸漬
した。脱銅ドロスはスラリー状になった。得られたスラ
リーをフィルタープレスにより濾過し、濾液を浸出滓よ
り分離した。 【0008】濃塩酸を使用するのは下記の理由による。 濃塩酸は常温で脱銅ドロスを粉砕等の前処理をすること
なく脱銅ドロスと反応し、下記の反応式により錫は第一
錫イオンとなり、水素を発生する。       Sn  +2HCl      ─→  
  Sn2++2Cl− +  H2   反応は可な
り激しいが脱銅ドロスを少量ずつ投入することにより制
御できない程ではない。金属錫の浸出率は濃塩酸を金属
錫に対して当量の2〜2.5倍程度使用すると90パー
セント以上になる。硫化銅の浸出は少量である。又残滓
は容易に濾過が可能である。これに対し希塩酸(2+1
)を使用すると、反応は穏やかであるが金属錫の浸出率
は80パーセント程度に止まる。硫化銅は溶解せず、従
って浸出液中に銅は殆ど含有されない。従って脱銅ドロ
スの性状が良好で浸出液中に銅を含有しないようにする
ときに適する。 【0009】比較のための実験によると、硫酸は脱銅ド
ロスと加熱しないと反応せず、且つ錫の浸出率が低い。 又硝酸は過度に激しく反応し、反応の制御が極めて困難
である。 【0010】濾液は水で約2倍量に希釈し4m3 にし
た。この濾液は主として塩化錫SnCl2 のの水溶液
でありSn112g/lを含有している。この水溶液を
耐酸性のセメンテーションタンク1に入れた。アルミニ
ウム片を含有するスクラップ400kgを耐酸性合成繊
維製の織り目が粗く液体が自由に通過可能な袋2に詰め
、袋2は梁3により水平に移動可能な昇降機4により降
下しセメンテーションタンク1に入れられ浸漬された。 アルミニウム片を含有するスクラップには錫が約10パ
ーセント、アルミニウムが約60パーセント、そのうち
金属アルミニウムが約50パーセント含まれている。錫
イオンは下記の反応式に従い袋2の中で金属錫として析
出した。         3Sn2++6Cl− +2Al  
─→  3Sn+2Al3++6Cl− 浸漬を継続す
るとセメンテーションタンク1中の錫イオンは順次減少
し、3日後にはSn0.10g/lを含有するのみとな
り、除去率は99.9パーセントに達した。又塩化アル
ミニウムの濃度は210g/lに昇った。 【0011】3日後に浸漬を終了し、袋2はセメンテー
ションタンク1より昇降機4により引上げられ、梁3に
より水平に移動し、昇降機4により降下し隣接した水洗
タンク5に入れて洗浄した。洗浄終了後再び袋2はセメ
ンテーションタンク1より昇降機4により引上げられ、
梁3により水平に移動し、昇降機4により降下し隣接し
た圧縮絞り機6に置かれ、袋2の内容物を袋2に入れた
まま圧縮し絞り脱水した。脱水後袋2は昇降機4により
引上げられ、梁3により水平に移動し、昇降機4により
降下し隣接したコンテナ7に移した。コンテナ7は溶錬
工場に送られた。 【0012】アルミニウム片を含有するスクラップを袋
2に入れて処理するのは、袋2に入れた後は浸漬、洗浄
、脱水、錫滓の溶錬工場への移送が一連の省力工程で実
行可能になるからである。又アルミニウム片による金属
錫の析出は錫とアルミニウムのイオン化傾向の相違に基
づくものであるから、何らの副資材を必要としないし、
析出した錫滓はそのまま何らの処理を要せず溶錬工場に
原料として送られる。 【0013】袋の内容物は錫約83パーセントと水分の
他少量の不純物を含む錫滓484kgであり、ドロス中
の錫の回収率は92.6パーセントであった。得られた
錫滓は溶錬工場に送り粗錫原料として斜板炉に投入した
。錫滓は既に金属に還元されているから、更なる電解が
不要であり、電気エネルギーを消費しない。セメンテー
ションタンク1に残留した液はAlCl3 溶液となり
凝集剤として廃液処理工程で有効に使用された。又、浸
出滓は硫化銅Cu2 Sが主成分であり、銅が2〜3倍
に濃縮されており、銅精錬工場に送り銅原料として利用
された。 【0014】次に脱銅ドロス、錫滓及び浸出滓(未乾燥
)の分析値一覧を示す。     分析値一覧                 Sn    Cu 
   S      Fe    Pb    As 
 Al( %)   脱銅ドロス     48   
   25       6      2.0   
  1.0     1.5            
浸出滓          7      65   
   10      2.5     1.0   
  1.5          アルミニウム   含有スクラップ 9.6     0.5  <0
.5     0.6      1.4    <0
.5 〜60    錫滓           83
      0.3  <0.5     0.2  
   <0.1   <0.1         【0
015】 【発明の効果】本発明により脱銅ドロスが処理され、錫
と併せて銅が回収された。又アルミニウム片を含有する
スクラップも容易に処理された。
DETAILED DESCRIPTION OF THE INVENTION [0001] The present invention relates to a copper-removal dross treatment method. More specifically, the present invention relates to a copper-free dross treatment method for treating copper-free dross mainly composed of metallic tin and copper sulfide generated during a tin refining process and recovering tin. [0002] Decoppered dross is produced during the tin refining process when copper contained in crude tin is removed as copper sulfide by adding sulfur. When copper is removed, a large amount of tin is mixed into the decoppered dross. R. A. Written by WRIGHT, “
Extractive Metalurgyof
Tin”, 2nd Ed. , ELSEVIER Publishers, 1982, p. 226, describes the post-treatment of decoppered dross by oxidative burning. [0003] However, in recent years, the availability of high-quality tin raw materials has decreased, and the use of poor-quality tin raw materials has increased from the viewpoint of effective resource utilization, and as a result, the amount of decoppered dross generated has increased. Due to the increasing number of people, it has become necessary to utilize them effectively. Post-processing of decoppered dross is difficult, and the oxidation roasting method has a strong tendency to generate and sinter a copper-tin alloy during roasting.
It was difficult to perform roasting, which is an easy post-processing process, and was not an appropriate processing method. There was no other suitable treatment method and it was not used effectively. On the other hand, there is an increasing amount of scrap containing a large amount of aluminum pieces in recovered tin raw materials, and it is required to easily process this together with copper-removed dross. SUMMARY OF THE INVENTION In view of the above-mentioned problems, an object of the present invention is to provide a method for easily recovering tin by processing dross, and also for processing scrap containing aluminum pieces. [Means for Solving the Problems] In the present invention, decoppered dross containing metallic tin and copper sulfide as main components is treated with hydrochloric acid to selectively leach tin, and the leachate and leach slag are separated. After that, a copper-removal dross treatment method was constructed in which the aluminum pieces were immersed in the leachate to recover tin. At the same time, a series of steps of immersion in the leachate, subsequent washing with water, and dehydration are carried out while the scrap containing the aluminum piece is placed in a container having good water permeability and flexibility. A processing method was constructed. [Operation] When decoppered dross containing metallic tin and copper sulfide as main components is immersed in concentrated hydrochloric acid at room temperature, the metallic tin generates hydrogen and dissolves, and the decoppered dross becomes a slurry. When solid-liquid separation is performed by conventional methods such as filtration, tin is added to the leachate from the decoppered dross.
0% or more is eluted and becomes a tin chloride SnCl2 solution. When aluminum pieces are immersed in leachate, metallic tin is precipitated and used as crude tin. The scrap containing the aluminum pieces is then preferably subjected to a series of soaking, rinsing and dewatering steps while still in a container having good water permeability and flexibility. Incidentally, the leaching slag is concentrated in copper to more than 60% and contains only a few percent in tin, so it is used as a raw material for copper refining. [Embodiment] An embodiment of the present invention will be explained with reference to FIG. FIG. 1 is a diagram showing a series of processing equipment for decoppered dross. One ton of decoppered dross was poured into 2 m3 of concentrated hydrochloric acid in an acid-resistant tank at room temperature little by little without being pulverized with stirring. Add hydrogen while monitoring the generation of hydrogen to prevent the reaction from becoming too intense. At this time, hydrogen sulfide is generated along with hydrogen, so provide local exhaust ventilation and be careful not to let the hydrogen concentration reach an explosive concentration. It takes about 2 liters to put in the entire 1 ton.
It took a while to finish. After that, stirring was continued and immersion was continued for 10 hours. The decoppered dross became a slurry. The resulting slurry was filtered using a filter press, and the filtrate was separated from the leachate. The reason for using concentrated hydrochloric acid is as follows. Concentrated hydrochloric acid reacts with decoppered dross at room temperature without pretreatment such as crushing the decoppered dross, and according to the reaction formula below, tin becomes stannous ions and hydrogen is generated. Sn +2HCl ─→
The Sn2++2Cl- + H2 reaction is quite violent, but not so much that it cannot be controlled by adding the decoppered dross little by little. The leaching rate of metallic tin becomes 90% or more when concentrated hydrochloric acid is used in an equivalent amount of 2 to 2.5 times the amount of metallic tin. Leaching of copper sulfide is small. Moreover, the residue can be easily filtered. In contrast, dilute hydrochloric acid (2+1
), the reaction is mild, but the leaching rate of metallic tin remains at about 80%. Copper sulfide does not dissolve, so the leachate contains almost no copper. Therefore, the decoppered dross has good properties and is suitable for preventing copper from being contained in the leachate. According to comparative experiments, sulfuric acid does not react with decoppered dross unless heated, and the leaching rate of tin is low. Furthermore, nitric acid reacts excessively violently, making it extremely difficult to control the reaction. [0010] The filtrate was diluted with water to approximately double the volume to 4 m3. This filtrate is mainly an aqueous solution of tin chloride, SnCl2, and contains 112 g/l of Sn. This aqueous solution was placed in an acid-resistant cementation tank 1. 400 kg of scrap containing aluminum pieces is packed into a bag 2 made of acid-resistant synthetic fiber with a coarse weave through which liquid can pass freely, and the bag 2 is lowered by an elevator 4 that can be moved horizontally by a beam 3 into a cementation tank 1. It was put in and soaked. Scrap containing aluminum pieces contains approximately 10 percent tin and approximately 60 percent aluminum, of which approximately 50 percent is metallic aluminum. Tin ions were precipitated as metallic tin in bag 2 according to the reaction formula below. 3Sn2++6Cl- +2Al
─→ 3Sn+2Al3++6Cl− As the immersion continued, the tin ions in the cementation tank 1 gradually decreased, and after 3 days, it contained only 0.10 g/l of Sn, and the removal rate reached 99.9%. Also, the concentration of aluminum chloride rose to 210 g/l. After 3 days, the soaking was completed, and the bag 2 was lifted up from the cementation tank 1 by the elevator 4, moved horizontally by the beam 3, lowered by the elevator 4, and placed in the adjacent washing tank 5 for cleaning. After cleaning, the bag 2 is lifted up again from the cementation tank 1 by the elevator 4.
It was moved horizontally by a beam 3, lowered by an elevator 4, and placed on an adjacent compressing and squeezing machine 6, where the contents of the bag 2 were compressed while remaining in the bag 2 and squeezed for dehydration. After dewatering, the bag 2 was lifted up by an elevator 4, moved horizontally by a beam 3, lowered by an elevator 4, and transferred to an adjacent container 7. Container 7 was sent to the smelting plant. [0012] The scrap containing aluminum pieces is placed in the bag 2 and processed through a series of labor-saving steps such as soaking, washing, dehydration, and transporting the tin slag to the smelting factory. This is because it becomes Furthermore, since the precipitation of metallic tin using aluminum pieces is based on the difference in ionization tendency between tin and aluminum, no auxiliary materials are required.
The precipitated tin slag is sent as raw material to a smelting factory without any treatment. The contents of the bag were 484 kg of tin slag containing approximately 83% tin and a small amount of impurities in addition to water, and the recovery rate of tin in the dross was 92.6%. The obtained tin slag was sent to a smelting factory and fed into a swash plate furnace as a crude tin raw material. Since the tin slag has already been reduced to metal, no further electrolysis is required and no electrical energy is consumed. The liquid remaining in the cementation tank 1 became an AlCl3 solution and was effectively used as a coagulant in the waste liquid treatment process. The leaching slag was mainly composed of copper sulfide (Cu2S), and the copper was concentrated two to three times, and was sent to a copper smelting factory and used as a raw material for copper. Next, a list of analytical values for decoppered dross, tin slag and leaching slag (undried) is shown. Analysis value list Sn Cu
S Fe Pb As
Al (%) Decoppered dross 48
25 6 2.0
1.0 1.5
Leach slag 7 65
10 2.5 1.0
1.5 Aluminum-containing scrap 9.6 0.5 <0
.. 5 0.6 1.4 <0
.. 5 ~60 Tin slag 83
0.3 <0.5 0.2
<0.1 <0.1 0
[015] According to the present invention, decoppered dross was treated and copper was recovered together with tin. Scrap containing aluminum pieces was also easily processed.

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

【図1】脱銅ドロスの一連の処理装置を示す図である。FIG. 1 is a diagram showing a series of processing equipment for decoppered dross.

【符号の説明】[Explanation of symbols]

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】  金属錫と硫化銅を主成分とする脱銅ド
ロスを塩酸により処理して錫を選択的に浸出し、浸出液
と浸出滓とを分離した後、浸出液中にアルミニウム片を
浸漬して錫を回収することを特徴とする脱銅ドロス処理
法。
[Claim 1] Copper-free dross containing metallic tin and copper sulfide as main components is treated with hydrochloric acid to selectively leach tin, and after separating the leachate and leach slag, aluminum pieces are immersed in the leachate. A copper-removal dross treatment method characterized by recovering tin.
【請求項2】  該浸出液中の浸漬及び引き続く水洗並
びに脱水の一連の工程を、該アルミニウム片を含有する
スクラップを良好な水透過性及び可撓性を有する容器中
に入れたままの状態で行うことを特徴とする請求項1に
記載された脱銅ドロス処理法。
2. A series of steps of immersion in the leachate and subsequent rinsing and dehydration are carried out while the scrap containing the aluminum pieces remains in a container having good water permeability and flexibility. The copper-removal dross treatment method according to claim 1.
JP8937191A 1991-03-29 1991-03-29 Metal tin recovery method Expired - Lifetime JP3060574B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8937191A JP3060574B2 (en) 1991-03-29 1991-03-29 Metal tin recovery method

Publications (2)

Publication Number Publication Date
JPH04304327A true JPH04304327A (en) 1992-10-27
JP3060574B2 JP3060574B2 (en) 2000-07-10

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* Cited by examiner, † Cited by third party
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TWI396595B (en) * 2010-04-07 2013-05-21 Univ Da Yeh A method for the recycling of tin waste
JP2020132981A (en) * 2019-02-25 2020-08-31 三和油化工業株式会社 Metal recovery method and metal recovery apparatus
CN113621821A (en) * 2021-08-20 2021-11-09 金隆铜业有限公司 Method for recovering metallic tin from lead-bismuth-removed Kaldo furnace slag
CN117568620A (en) * 2023-12-01 2024-02-20 昆明理工大学 Crude tin double-pot sulfur adding and impurity removing reactor

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI396595B (en) * 2010-04-07 2013-05-21 Univ Da Yeh A method for the recycling of tin waste
JP2020132981A (en) * 2019-02-25 2020-08-31 三和油化工業株式会社 Metal recovery method and metal recovery apparatus
CN113621821A (en) * 2021-08-20 2021-11-09 金隆铜业有限公司 Method for recovering metallic tin from lead-bismuth-removed Kaldo furnace slag
CN117568620A (en) * 2023-12-01 2024-02-20 昆明理工大学 Crude tin double-pot sulfur adding and impurity removing reactor
CN117568620B (en) * 2023-12-01 2024-04-30 昆明理工大学 Crude tin double-pot sulfur adding and impurity removing reactor

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