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JP3535629B2 - Recycling of valuable metals from scraps - Google Patents

Recycling of valuable metals from scraps

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Publication number
JP3535629B2
JP3535629B2 JP25829695A JP25829695A JP3535629B2 JP 3535629 B2 JP3535629 B2 JP 3535629B2 JP 25829695 A JP25829695 A JP 25829695A JP 25829695 A JP25829695 A JP 25829695A JP 3535629 B2 JP3535629 B2 JP 3535629B2
Authority
JP
Japan
Prior art keywords
scrap
furnace
scraps
copper
flash
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
JP25829695A
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Japanese (ja)
Other versions
JPH0978151A (en
Inventor
近志 末永
毅 御手洗
直人 中山
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.)
Nippon Mining Holdings Inc
Original Assignee
Nippon Mining and Metals 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 Nippon Mining and Metals Co Ltd filed Critical Nippon Mining and Metals Co Ltd
Priority to JP25829695A priority Critical patent/JP3535629B2/en
Priority to KR1019960031589A priority patent/KR100311653B1/en
Publication of JPH0978151A publication Critical patent/JPH0978151A/en
Application granted granted Critical
Publication of JP3535629B2 publication Critical patent/JP3535629B2/en
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Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • 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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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Description

【発明の詳細な説明】 【0001】 【発明の属する技術分野】本発明は、銅、金、銀、およ
び白金等の有価金属を含有するスクラップ類を銅鉱石溶
錬用自溶炉において処理し、スクラップ類からの有価金
属をリサイクルする方法に関するものである。 【0002】 【従来の技術】近年、電子部品製造業やそれら電子部品
を利用する製品および産業から発生するスクラップ類
(電線屑、リードフレーム、ICチップ、樹脂付き基板
屑、超小型コイル、スイッチ等々)の発生量が大幅に増
大する傾向にある。これらスクラップ類には、電気導体
として使われる銅や、接点、メッキ皮膜等に使用された
金、銀、白金、パラジウム等の有価金属が含まれてお
り、この有価金属の回収は、資源のリサイクルによる省
資源の観点からも重要である。 【0003】上記のようなスクラップ類はもちろん以前
からも発生しており、そのリサイクル方法は多様であ
る。銅分が多くて、他の有価金属(貴金属)の含有率が
低ければ、単純に、溶融した銅の中にスクラップ類を投
入し、銅を回収することができる。 【0004】また、貴金属を含有しているスクラップを
焼却(有機絶縁物を燃焼させ)し、燃焼後の灰に有価金
属を濃縮する方法がある。しかし、この方法では有価金
属の一部が酸化されるため、有価金属を回収するために
は、焼却灰を原料に金属の精練を行なう必要がある。 【0005】一方、スクラップ中の有価金属を酸化させ
ず回収する方法としては、例えば、特開昭49−531
23に記載される方法がある。これは絶縁電線スクラッ
プを溶融した鉛の中へ浸漬することにより、空気を遮断
した状態で有機絶縁物を熱分解し燃料として回収し、さ
らに銅分を酸化させずに回収する方法である。同様の方
法として、特開昭53−16302は、密閉容器内でス
クラップを加圧・加熱しスクラップ中の絶縁物(ポリ塩
化ビニール、ゴム、ポリウレタン、テフロン等の樹脂)
を分解して除去することにより、金属を未酸化の状態で
回収する方法を開示している。しかしながら、これら方
法は処理量に限界があり、工程が面倒である。 【0006】ところで、以上のような、スクラップのみ
を処理(あるいは予備処理)する方法とは異なり、スク
ラップ類を直接、銅製錬工程で処理する方法も実施され
ている。一般的に行なわれている方法は、上記スクラッ
プ類をボートに積載し、これをクレーンを使って持ち上
げ、スクラップ類を銅製錬転炉(PS転炉)へ装入する
ものである。この方法では、転炉内溶湯の強烈な撹拌効
果および炉内反応熱を利用して、非自然性のスクラップ
でも容易にスラグ化して溶解することができる点で有利
である。またスクラップ中の銅、金および銀等の有価金
属は、98%を超える高い収率で転炉内のマットすなわ
ちカワ(あるいは粗銅)へ回収される。上記の天井クレ
ーンで投入する方法では、スクラップを炉内へ装入する
ために、転炉の送風を一時中断し、かつ転炉を傾転させ
なければならず、転炉稼動率の低下および亜硫酸ガスの
炉内からの漏洩といった問題が生じている。これらの問
題を解決する方法として、スクラップ類を転炉炉頂から
シュートを使って投入する方法がある。また、特開平6
−287655のように、不良アノード投入のための搬
送装置、移載装置、搬送投入装置を転炉炉頂に設置し、
この装置を使って不良アノードを転炉内へ側面扉を通し
て投入するに際して不良アノード上にスクラップ類を載
置して一緒に転炉内へ投入する方法もある。 【0007】 【発明が解決しようとする課題】以上のように、転炉で
処理する場合、燃料および予備処理をほとんど必要とせ
ず、かつ銅の製錬と同時に行なえるという利点がある。
しかし、上述の転炉で処理する方法のうち、スクラップ
を炉頂からシュートを通して、あるいはボートに積載し
て投入する場合、炉体への悪影響があった。すなわち、
スクラップ類中の有機絶縁物は一般に300℃以下で熱
分解を起こすので、炉内に投入された直後に熱分解によ
り水素ガスおよび炭素ヒューム等を発生する。これら熱
分解生成物は、酸素濃度の低い炉内では燃焼せず、転炉
排ガスフード近傍でフリーエアーと混合されて燃焼し、
転炉排ガスフードを高温に加熱し、排ガスフードの損耗
を促進する。 【0008】さらに、スクラップ中の有機絶縁物(合成
樹脂類)から揮発した有機物の一部が完全に分解・燃焼
されず、転炉排ガスを原料に製造している製品硫酸に吸
収され着色する等の問題がある。 【0009】本発明の課題は、スクラップ類の転炉処理
に変わる新たな工業的リサイクル方法を確立することで
ある。 【0010】 【課題を解決するための手段】一般的に云って、銅製錬
工程で直接処理する方法が予備処理をほとんど要しない
ため処理コストが低く、スクラップ中の有価金属含有率
が低くても回収率および大量処理に問題がないため、リ
サイクル法として望ましい。そこで、前記転炉処理に伴
う、排ガスフードの損耗および製品硫酸への着色といっ
た問題点を解決するため、本発明者は、スクラップ類を
銅鉱石溶錬用自溶炉で処理することを想到した。転炉と
違って、密閉式の自溶炉ではスクラップ中の有機絶縁物
(合成樹脂類)から揮発した有機物が完全に分解・燃焼
するので、製品硫酸への着色を避けることができる。 【0011】一方、自溶炉で処理する方法においても、
有価金属分の割合が少なく、合成樹脂、無機絶縁物(ガ
ラスファイバー等)が多く含まれているスクラップを処
理する場合には、新たな問題が生じる。すなわち、自溶
炉では溶湯直上の酸素濃度が極めて低いため、単純に自
溶炉セトラー部から投入しても雰囲気酸素濃度が低いた
め、完全には燃焼せず、溶湯表面(スラグの上)に浮上
してしまうといった問題点がある。さらに、転炉に比べ
て自溶炉内溶湯の撹拌効果は小さいので、スクラップ中
の熱分解残留物および無機絶縁物がスラグ化しない。こ
のため、スクラップ中の有価金属のマットへの移行(沈
降)が妨げられる。また、セトラー部から大量に投入し
た場合、合成樹脂類から発生した有機物が自溶炉排ガス
とともにボイラーへ導かれ、ボイラー内で燃焼し、ボイ
ラー内温度を上昇させることにより、自溶炉ダストのボ
イラー水管への融着を誘発する。 【0012】スクラップ類の自溶炉での処理を実現する
ためには、これら問題点を克服する必要がある。本発明
者らは、研究を重ねた結果、スクラップ類を自溶炉のシ
ャフト天井部から投入することにより、これら問題点を
解決してスクラップ類の自溶炉処理の実用化が可能とな
ることを見出した。かくして、本発明は、有価金属を含
有するスクラップ類を銅鉱石溶錬用自溶炉へシャフト天
井部から装入し、有価金属を炉内に滞留するマットへ回
収することを特徴とするスクラップ類からの有価金属の
リサイクル方法を提供する。スクラップ類を予め粉砕し
ておき、これを銅鉱石溶錬用装入物と混合して自溶炉精
鉱バーナーから炉内へ装入することが最も実用的であ
る。 【0013】 【発明の実施の形態】銅鉱石溶錬用自溶炉は、図1に示
すように、シャフト1、セットラー2及びアップテイク
3から構成され、シャフト1にはその天井部4において
1〜4本の精鉱バーナー5が装備されている。精鉱バー
ナから銅鉱石溶錬用装入物を、一般に微粉精鉱を溶剤
(フラックス)と共に酸素富化空気乃至酸素或いは高温
熱風と同時に吹込み、瞬間的に酸化反応を起こさせる。
酸化反応熱のみでは熱量が不足するので、通常精鉱バー
ナーから重油を助燃する。シャフトを通しての落下中、
精鉱は1300℃以上の高温で溶融し、セットラーにお
いて、50〜68%の銅を含むマット(カワ、硫化物融
体)とその上方に浮遊するスラグ(カラミ)に分離す
る。セットラーにはその側面にスラグホールとマットホ
ールとが形成されている(図示省略)。一方、排ガスは
約1300℃の高温で10%前後のSO2 を含有してお
り、アップテイク3から付帯設備の廃熱ボイラー6に通
される。ボイラーにおいて熱を回収した後、冷却された
排ガスは、電気集塵機でダストを捕集した後、硫酸工場
に送られ、硫酸を製造する。 【0014】本発明に従えば、スクラップ類からの有価
金属のリサイクル方法として、有価金属を含有するスク
ラップ類は、銅鉱石溶錬用自溶炉へシャフト1の天井部
4から装入され、有価金属を炉内に滞留するマット(硫
化物融体)へ回収することを特徴とする。スクラップ類
用の装入口を天井部に別途設けてもよいが、スクラップ
類を予め粉砕しておき、これを銅鉱石精鉱及び溶剤と混
合して自溶炉精鉱バーナー5から炉内へ装入することが
好ましい。特に、スクラップ類の中でも難燃性および難
溶融性のものについては、40mm以下、好ましくは1
0mm以下に、より好ましくは2mm以下に粉砕して、
自溶炉精鉱バーナーから鉱石とともに炉内へ装入する。
スクラップ類の粉砕は適宜の粉砕ミルを使用して行えば
よいが、自溶炉用の溶剤(硅石)の粉砕と同時に行なう
のが便宜であり、ほとんどコスト増にはならない。 【0015】これにより、スクラップはシャフト落下途
中に鉱石とともに1300℃以上の高温で燃焼・溶融
し、溶湯に到達後、速やかに有価金属がマットに吸収さ
れる。また、スクラップ中のSiO2 等の不燃分も速や
かにスラグに吸収される。この際、一部の有価金属は、
シャフト落下中に酸化物になると考えられるが、溶融鉱
石粒子から供給される硫化鉄により還元(硫化)され、
マット(硫化物相)へ吸収される。 【0016】また、この方法では、スクラップがシャフ
ト直下の溶湯の広い範囲に均等に分散されるので、シャ
フト落下中の燃焼・溶融が多少遅れたスクラップがあっ
たとしても、セトラー部の1ヶ所に集中的に投入する場
合に比べて、溶湯到達後の溶解および不要分のスラグ化
が容易である。さらに、スクラップ中の合成樹脂類から
熱分解で発生する有機物が、自溶炉内を通過する間に完
全に分解・酸化されるので、ボイラー内で燃焼すること
がない。有機絶縁物中に塩素、フッ素等のハロゲン元素
が含まれる場合には、硫酸製造工程の予備処理段階で除
去することができる。 【0017】 【実施例】電気部品屑を主体とするスクラップを粉砕し
て自溶炉へ装入する操業を行なった。 (i)粉砕前のスクラップ 粉砕前のスクラップの粒度は、最大80mm程度、最小
20mm程度のものが主体であり、基板や銅線コードも
多く含まれていた。処理されたスクラップ全体としての
平均的な成分分析値は次の表1の通りである。無機絶縁
物も含まれているため、SiO2 含有率が高い。 【0018】 【表1】 【0019】(ii)粉砕方法および粉砕粒度 粉砕は、自溶炉用の溶剤(フラックス)として通常使用
している硅石の粉砕用のボールミルを用いて、硅石と一
緒(同時)に行なった。粉砕後のスクラップ粒度分布は
表2のとおりである。 【0020】 【表2】 【0021】(iii)自溶炉への装入 スクラップは、粉砕中に硅石と混合されているが、これ
を、さらに銅鉱石と混合してから、乾燥した後、自溶炉
シャフト天井部に設置された精鉱バーナーから炉内に装
入した。尚、鉱石およびスクラップの装入速度は以下の
通りとした: 鉱石装入量 :65 Ton/Hr スクラップ装入量:0.55 Ton/Hr 【0022】(iv)有価物の回収 自溶炉に装入された有価金属は、マットに吸収され次工
程の転炉へ送られることになるが、スラグに含まれて排
出される分がロスとなる。図2に、試験期間中の自溶炉
スラグ中の銅含有率を示す。試験期間中のスラグ中の銅
含有率は、通常操業と差がなく、スクラップ中の銅がロ
スすることなくマットに吸収されていたことがわかる。 【0023】金、銀についても、銅と同様にマットへ回
収されることになる。図3に試験期間中のマットの金、
銀含有率の推移を示す。この図3から判るようにマット
中の金、銀含有率が試験操業開始とともに上昇してお
り、マットへ金、銀が回収されていたことが判る。 【0024】次に有価金属のマットへの回収率を調べる
ために、スラグへの銀のロス率を評価する。スラグへの
銀のロスは、溶融スラグ中に懸垂しているマット粒子に
含まれている分がほとんどであるから、スクラップ装入
によりマット中の銀含有率が上昇したことも加味して評
価する必要がある。よって、スラグ/マット間の分配係
数(=スラグ中含有率/マット中含有率)で評価するの
が妥当である。試験期間中の銀の分配係数の推移を図4
に示す。図4から判るように銀の分配係数は、どちらも
通常操業時と差がない。これによって、スクラップ中の
銀のマットへの回収率は、通常操業時の鉱石からの回収
率(99%以上)と同等であったと判断することができ
る。 【0025】(v)製品硫酸への着色及びボイラー温度
への影響 更に、製品硫酸への着色及びボイラー温度の上昇程度を
調べた結果、スクラップの自溶炉装入試験操業の影響
で、自溶炉排ガスを原料に製造する製品硫酸を着色させ
ることはなかった。スクラップに含まれる有機絶縁体は
完全に分解・燃焼していたと考えられる。スクラップの
自溶炉装入試験操業の影響で、ボイラー温度が上昇する
ことはなかった。自溶炉シャフト、セトラー部でスクラ
ップの熱分解・燃焼が完了していた。 【0026】 【発明の効果】本発明によれば、銅溶錬自溶炉での銅製
錬にスクラップ処理を組み合わせるため、有価金属含有
率が低いスクラップ類からでも、低コストで有価金属を
回収することができる。難燃性のスクラップ類の場合
は、予め粉砕を行なわなくてはならないが、この粉砕も
自溶炉用の溶剤(硅石)の粉砕と同時に行なえばよいの
で、ほとんどコスト増にはならない。また、有機絶縁物
を溶錬炉内で確実に熱分解・燃焼することができるの
で、溶錬炉排ガスを硫酸製造工程で処理しても製品硫酸
の品質を悪化させることはない。さらに、有機絶縁物中
に含まれる塩素、フッ素等のハロゲン元素は、硫酸製造
工程の予備処理段階で除去できるので、新たに公害防止
のためのガス処理設備を設けなくてもよい。銅溶錬自溶
炉自体の改修や操業条件の変更は実質上必要でない。以
上のように、従来の方法では処理コストが見合わず、最
終処分に困るような産業廃棄物にも適用できるため、省
資源のみならず環境保護にも役立つ。
Description: BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method of processing scraps containing valuable metals such as copper, gold, silver and platinum in a flash smelting furnace for smelting copper ore. And a method for recycling valuable metals from scraps. 2. Description of the Related Art In recent years, scraps generated from the electronic component manufacturing industry and products and industries that use those electronic components (electric wire scraps, lead frames, IC chips, resinous board scraps, microminiature coils, switches, etc.) ) Tends to increase significantly. These scraps contain copper used as electrical conductors, and valuable metals such as gold, silver, platinum, and palladium used for contacts and plating films. These valuable metals are collected by recycling resources. It is also important from the viewpoint of resource saving. [0003] Scraps as described above have naturally been generated, and recycling methods are diverse. If the copper content is high and the content of other valuable metals (precious metals) is low, scraps can simply be put into the molten copper to recover the copper. Further, there is a method of incinerating a scrap containing a noble metal (burning an organic insulator) and concentrating a valuable metal in ash after burning. However, in this method, a part of the valuable metal is oxidized. Therefore, in order to recover the valuable metal, it is necessary to refine the metal using incinerated ash as a raw material. On the other hand, as a method of recovering valuable metals in scrap without oxidizing, for example, JP-A-49-531
23. In this method, an insulated wire scrap is immersed in molten lead to thermally decompose an organic insulator in a state where air is shut off and collect it as a fuel, and further collect copper without oxidizing it. As a similar method, JP-A-53-16302 discloses that a scrap is pressurized and heated in an airtight container, and an insulator (a resin such as polyvinyl chloride, rubber, polyurethane, or Teflon) is contained in the scrap.
Discloses a method of recovering a metal in an unoxidized state by decomposing and removing the metal. However, these methods have a limited throughput and are cumbersome. By the way, unlike the above-described method of treating only scrap (or pretreatment), a method of directly treating scraps in a copper smelting process is also practiced. A commonly practiced method is to load the scraps on a boat, lift the scraps using a crane, and load the scraps into a copper smelting converter (PS converter). This method is advantageous in that even unnatural scrap can be easily turned into slag and melted by utilizing the strong stirring effect of the molten metal in the converter and the reaction heat in the furnace. In addition, valuable metals such as copper, gold and silver in the scrap are recovered to a mat in the converter, that is, to the Kawa (or blister copper) with a high yield exceeding 98%. In the above-mentioned method using the overhead crane, in order to load the scrap into the furnace, the ventilation of the converter must be temporarily stopped, and the converter must be tilted. There is a problem that gas leaks from the furnace. As a method for solving these problems, there is a method of throwing scraps from the converter furnace top using a chute. In addition, Japanese Unexamined Patent Publication
As in -287655, a transfer device for transferring defective anodes, a transfer device, and a transfer charging device are installed on the converter furnace top,
When a defective anode is charged into a converter through a side door using this apparatus, there is a method in which scraps are placed on the defective anode and then charged together into the converter. [0007] As described above, when the treatment is performed in the converter, there is an advantage that the fuel and the pretreatment are hardly required, and the treatment can be performed simultaneously with the smelting of copper.
However, among the above-described methods of processing in a converter, when scrap is loaded from a furnace top through a chute or loaded on a boat, there is an adverse effect on the furnace body. That is,
Since organic insulators in scraps generally undergo thermal decomposition at a temperature of 300 ° C. or lower, hydrogen gas and carbon fumes are generated by thermal decomposition immediately after being placed in a furnace. These pyrolysis products do not burn in a furnace with a low oxygen concentration, but mix and burn with free air near the converter exhaust hood,
The converter exhaust hood is heated to a high temperature to promote wear of the exhaust hood. Further, some of the organic substances volatilized from the organic insulators (synthetic resins) in the scrap are not completely decomposed and burned, and are absorbed and colored by the sulfuric acid in the product produced from the converter exhaust gas. There is a problem. [0009] It is an object of the present invention to establish a new industrial recycling method replacing the converter treatment of scraps. [0010] Generally speaking, the method of direct treatment in the copper smelting process requires little pretreatment, so that the treatment cost is low and even if the content of valuable metals in scrap is low. It is desirable as a recycling method because there is no problem in recovery rate and mass processing. Therefore, in order to solve the problems of exhaust gas hood wear and coloring of the product sulfuric acid due to the converter treatment, the present inventor has conceived of treating scraps in a flash smelting furnace for smelting copper ore. . Unlike a converter, in a closed type flash smelting furnace, organic substances volatilized from organic insulators (synthetic resins) in scrap are completely decomposed and burned, so that coloring of the product sulfuric acid can be avoided. On the other hand, in the method of processing in a flash furnace,
A new problem arises when processing scrap containing a small proportion of valuable metals and containing a large amount of synthetic resin and inorganic insulators (such as glass fiber). That is, in the flash smelting furnace, the oxygen concentration immediately above the molten metal is extremely low, so even if the oxygen is simply introduced from the flash smelter settler, the atmospheric oxygen concentration is low. There is a problem that it will surface. Further, since the effect of stirring the molten metal in the flash smelting furnace is small as compared with the converter, the pyrolysis residue and the inorganic insulator in the scrap are not turned into slag. For this reason, transfer (sedimentation) of the valuable metal in the scrap to the mat is prevented. In addition, when a large amount is injected from the settler part, organic matter generated from synthetic resins is guided to the boiler together with the flue gas of the smelting furnace, burns in the boiler, and raises the temperature in the boiler, thereby increasing the boiler temperature of the smelting furnace dust. Induces fusion to the water tube. In order to realize the processing of scraps in a flash furnace, it is necessary to overcome these problems. As a result of repeated studies, the present inventors have found that by charging scraps from the shaft ceiling of the flash smelting furnace, these problems can be solved and the flash smelting treatment of scraps can be put to practical use. Was found. Thus, the present invention is characterized in that scraps containing valuable metals are loaded into a flash smelting furnace for smelting copper ore from a shaft ceiling portion, and the valuable metals are collected on a mat retained in the furnace. To provide a recycling method for valuable metals. It is most practical to grind the scraps in advance, mix them with the charge for smelting copper ore, and charge the scrap from the flash smelter concentrate burner into the furnace. DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS As shown in FIG. 1, a flash smelting furnace for smelting copper ore is composed of a shaft 1, a settler 2 and an uptake 3. Equipped with one to four concentrate burners 5. A charge for copper ore smelting is injected from a concentrate burner, and generally a fine concentrate is blown together with a solvent (flux) simultaneously with oxygen-enriched air or oxygen or high-temperature hot air to cause an instantaneous oxidation reaction.
Since the calorific value is insufficient with only the heat of oxidation reaction, heavy oil is usually burned from a concentrate burner. While falling through the shaft,
The concentrate melts at a high temperature of 1300 ° C. or higher and is separated in a settler into a mat (kawa, sulfide melt) containing 50 to 68% of copper and a slag (kalami) floating above the mat. A slug hole and a mat hole are formed on the side surface of the setler (not shown). On the other hand, the exhaust gas contains about 10% SO 2 at a high temperature of about 1300 ° C., and is passed from the uptake 3 to the waste heat boiler 6 of the incidental equipment. After recovering heat in the boiler, the cooled exhaust gas is sent to a sulfuric acid plant after collecting dust with an electric dust collector, and produces sulfuric acid. According to the present invention, as a method of recycling valuable metals from scraps, scraps containing valuable metals are charged from a ceiling 4 of a shaft 1 into a flash smelting furnace for smelting copper ore. It is characterized in that the metal is collected in a mat (sulfide melt) retained in the furnace. A loading port for scraps may be separately provided on the ceiling, but the scraps are crushed in advance, mixed with copper ore concentrate and a solvent, and loaded into the furnace from the flash smelter concentrate burner 5. Preferably. In particular, among the scraps, those having a flame retardancy and a low melting point are 40 mm or less, preferably 1 mm or less.
Crushed to 0 mm or less, more preferably 2 mm or less,
Charged into the furnace together with the ore from the flash smelter concentrate burner.
Scraps may be pulverized by using an appropriate pulverizing mill. However, it is convenient to perform the pulverization simultaneously with the pulverization of the solvent (silica) for the flash smelting furnace, and the cost is hardly increased. As a result, the scrap burns and melts together with the ore at a high temperature of 1300 ° C. or more while falling down the shaft, and the valuable metal is quickly absorbed by the mat after reaching the molten metal. Incombustible components such as SiO 2 in the scrap are also quickly absorbed by the slag. At this time, some valuable metals
It is considered to be oxide when the shaft falls, but it is reduced (sulfided) by iron sulfide supplied from the molten ore particles,
Absorbed by the mat (sulfide phase). Further, in this method, since the scrap is evenly distributed over a wide range of the molten metal just below the shaft, even if there is some delay in the combustion and melting during the fall of the shaft, the scrap is located in one place in the settler portion. Dissolving after the molten metal has been reached and unnecessary slag are easier than in the case of intensive charging. Further, since organic matter generated by thermal decomposition from synthetic resins in the scrap is completely decomposed and oxidized while passing through the flash furnace, it does not burn in the boiler. When a halogen element such as chlorine or fluorine is contained in the organic insulator, it can be removed in a pretreatment stage of the sulfuric acid production process. EXAMPLE An operation was carried out in which scrap mainly composed of electric component waste was pulverized and charged into a flash smelting furnace. (I) Scrap before crushing The size of scrap before crushing is mainly about 80 mm at the maximum and about 20 mm at the minimum, and many substrates and copper wire cords are included. Table 1 below shows the average component analysis value of the whole processed scrap. Since an inorganic insulator is also included, the content of SiO 2 is high. [Table 1] (Ii) Pulverization Method and Pulverization Particle Size Pulverization was carried out together with (simultaneously with) silica using a ball mill for pulverizing silica commonly used as a solvent (flux) for a flash furnace. Table 2 shows the scrap particle size distribution after pulverization. [Table 2] (Iii) The scrap charged into the flash smelting furnace is mixed with silica during the pulverization. The mixed scrap is further mixed with copper ore, and then dried. It was charged into the furnace from the installed concentrate burner. The ore and scrap loading rates were as follows: ore loading: 65 Ton / Hr scrap loading: 0.55 Ton / Hr (iv) Recovery of valuable resources The charged valuable metal is absorbed by the mat and sent to the converter in the next process, but the waste contained in and discharged from the slag becomes a loss. FIG. 2 shows the copper content in the flash slag during the test. It can be seen that the copper content in the slag during the test period was not different from that in the normal operation, and that the copper in the scrap was absorbed by the mat without loss. Gold and silver are also collected on the mat similarly to copper. Figure 3 shows the gold on the mat during the test.
The transition of the silver content is shown. As can be seen from FIG. 3, the content of gold and silver in the mat increased with the start of the test operation, indicating that gold and silver were collected on the mat. Next, in order to examine the recovery rate of valuable metals to the mat, the loss rate of silver to slag is evaluated. Most of the silver loss to the slag is included in the mat particles suspended in the molten slag, so it is also evaluated taking into account that the silver content in the mat has increased due to the charging of scrap. There is a need. Therefore, it is appropriate to evaluate by the distribution coefficient between slag and mat (= content in slag / content in mat). Figure 4 shows the transition of the silver distribution coefficient during the test period.
Shown in As can be seen from FIG. 4, the distribution coefficients of silver are not different from those in normal operation. Thereby, it can be determined that the recovery rate of silver in the scrap on the mat was equal to the recovery rate (99% or more) from the ore during the normal operation. (V) Coloring of Product Sulfuric Acid and Influence on Boiler Temperature Further, the coloring of product sulfuric acid and the degree of increase in boiler temperature were examined. The product sulfuric acid produced from the furnace exhaust gas was not colored. It is considered that the organic insulator contained in the scrap was completely decomposed and burned. The boiler temperature did not rise as a result of the scrap flash furnace charging test operation. Pyrolysis and combustion of scrap were completed in the flash furnace shaft and settler section. According to the present invention, since scrap processing is combined with copper smelting in a copper smelting flash furnace, valuable metals can be recovered at low cost even from scraps having a low content of valuable metals. be able to. In the case of flame-retardant scraps, pulverization must be performed in advance. However, since the pulverization may be performed simultaneously with the pulverization of the solvent (silica) for the flash furnace, the cost hardly increases. Further, since the organic insulator can be reliably thermally decomposed and burned in the smelting furnace, the quality of the product sulfuric acid does not deteriorate even if the smelting furnace exhaust gas is treated in the sulfuric acid production process. Further, since halogen elements such as chlorine and fluorine contained in the organic insulator can be removed in the preliminary treatment stage of the sulfuric acid production process, it is not necessary to newly provide a gas treatment facility for preventing pollution. Refurbishment of the copper smelting flash furnace itself and changes in operating conditions are virtually unnecessary. As described above, the conventional method does not meet the treatment cost, and can be applied to industrial waste that is difficult to dispose of finally, so that it is useful not only for resource saving but also for environmental protection.

【図面の簡単な説明】 【図1】銅鉱石溶錬用自溶炉及び廃熱ボイラーの該略図
である。 【図2】試験期間中の自溶炉スラグ中の銅含有率を示す
グラフである。 【図3】試験期間中のマットの金、銀含有率の推移を示
すグラフである。 【図4】試験期間中の銀の分配係数の推移を示すグラフ
である。 【符号の説明】 1 シャフト 2 セットラー 3 アップテイク 4 天井部 5 精鉱バーナー 6 廃熱ボイラー
BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a schematic view of a flash smelting furnace for copper ore smelting and a waste heat boiler. FIG. 2 is a graph showing a copper content in a flash slag during a test. FIG. 3 is a graph showing changes in the gold and silver contents of the mat during the test period. FIG. 4 is a graph showing a change in a distribution coefficient of silver during a test period. [Description of Signs] 1 Shaft 2 Settler 3 Uptake 4 Ceiling 5 Concentrate burner 6 Waste heat boiler

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 昭62−13543(JP,A) (58)調査した分野(Int.Cl.7,DB名) C22B 1/00 - 61/00 ────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-62-13543 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) C22B 1/00-61/00

Claims (1)

(57)【特許請求の範囲】 【請求項1】 有機絶縁物、無機絶縁物を含み且つ銅、
金、銀、白金及びパラジウムの群から選ばれた少なくと
も一種の有価金属を含有するスクラップ類を自溶炉用溶
剤と共に粉砕し、これを銅鉱石溶錬用装入物と混合して
銅鉱石溶錬用自溶炉へ自溶炉精鉱バーナーから装入し、
自溶炉を操業して前記有価金属を炉内に滞留するマット
へ回収することを特徴とするスクラップ類からの前記
価金属のリサイクル方法であり、スクラップ中の有機絶
縁物から揮発した有機物が完全に分解・燃焼し、製品硫
酸への着色を避けることができる前記有価金属のリサイ
クル方法。
(57) [Claims 1 organic insulator, inorganic insulator only containing and copper,
At least selected from the group of gold, silver, platinum and palladium
Also, scraps containing a kind of valuable metal are crushed together with the solvent for flash smelting furnace, mixed with the charge for copper ore smelting, and sent to the copper smelting flash smelting furnace from the flash smelting furnace. Charge
Is said chromatic <br/> valent metal recycling method from scrap such that and recovering the mat staying in the furnace of the valuable metal by operating a flash smelting furnace, an organic insulation in scrap
The recycling method of the valuable metal, wherein the organic matter volatilized from the rim is completely decomposed and burned to prevent coloring of the product sulfuric acid.
JP25829695A 1995-09-12 1995-09-12 Recycling of valuable metals from scraps Expired - Lifetime JP3535629B2 (en)

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KR1019960031589A KR100311653B1 (en) 1995-09-12 1996-07-30 Recycling of Valuable Metals from Scraps

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JP3535629B2 true JP3535629B2 (en) 2004-06-07

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