JPH0978151A - Recycle method of valuable metals from scraps - Google Patents
Recycle method of valuable metals from scrapsInfo
- Publication number
- JPH0978151A JPH0978151A JP25829695A JP25829695A JPH0978151A JP H0978151 A JPH0978151 A JP H0978151A JP 25829695 A JP25829695 A JP 25829695A JP 25829695 A JP25829695 A JP 25829695A JP H0978151 A JPH0978151 A JP H0978151A
- Authority
- JP
- Japan
- Prior art keywords
- scraps
- furnace
- scrap
- valuable metals
- smelting
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working 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
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- 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)
Abstract
Description
【0001】[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。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention processes scraps containing valuable metals such as copper, gold, silver and platinum in a copper ore smelting flash furnace to recycle valuable metals from scraps. It is about the method.
【0002】[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。2. Description of the Related Art In recent years, scraps (electric wire scraps, lead frames, IC chips, resin-containing board scraps, ultra-small coils, switches, etc.) are generated in the electronic parts manufacturing industry and products and industries using those electronic parts. The amount tends to increase significantly. These scraps include copper used as electrical conductors and valuable metals such as gold, silver, platinum, and palladium used for contacts and plated coatings. The recovery of these valuable metals is a recycling of resources. It is also important from the viewpoint of resource saving.
【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。The above-mentioned scraps, of course, have been generated even before, and there are various recycling methods. If the amount of copper is large and the content of other valuable metals (noble metals) is low, scraps can be simply put into molten copper to recover copper.
【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。There is also a method of incinerating scrap containing a noble metal (burning an organic insulator) and concentrating valuable metal in the ash after burning. However, in this method, a part of the valuable metal is oxidized, and therefore, in order to recover the valuable metal, it is necessary to refine the metal from the incinerated ash as a raw material.
【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。On the other hand, as a method for recovering valuable metal in scrap without oxidizing it, for example, Japanese Patent Application Laid-Open No. 49-531.
23. This is a method in which the insulated wire scrap is immersed in molten lead to thermally decompose the organic insulating material in the state where the air is cut off and to recover it as a fuel, and further to recover the copper content without oxidizing it. As a similar method, JP-A-53-16302 discloses pressurizing and heating scrap in an airtight container to insulate the scrap (resin such as polyvinyl chloride, rubber, polyurethane and Teflon).
It 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 the process is troublesome.
【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。By the way, unlike the above-described method of treating only scrap (or pretreatment), a method of directly treating scraps in a copper smelting step is also practiced. A commonly practiced method is to load the above 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 non-natural scrap can be easily slagged and melted by utilizing the strong stirring effect of the molten metal in the converter and the reaction heat in the furnace. Valuable metals such as copper, gold and silver in scrap are recovered in a mat, that is, a river (or blister) in a converter with a high yield of over 98%. In the above method of charging with an overhead crane, in order to load scrap into the furnace, it is necessary to suspend the air blowing of the converter and tilt the converter. There is a problem such as leakage of gas from the furnace. As a method of solving these problems, there is a method of charging scraps from the converter furnace top using a chute. In addition, Japanese Unexamined Patent Publication
As shown in -287655, a transfer device for transferring a defective anode, a transfer device, and a transfer input device are installed on the top of the converter furnace.
There is also a method in which scraps are placed on the defective anode and charged into the converter together when the defective anode is charged into the converter through the side door using this apparatus.
【0007】[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。As described above, the treatment in the converter has the advantages that it requires almost no fuel and pretreatment and can be performed simultaneously with the smelting of copper.
However, among the methods of processing in the above-mentioned converter, when scrap is introduced from the furnace top through the chute or loaded on a boat, it has an adverse effect on the furnace body. That is,
Since the organic insulator in the scraps generally undergoes thermal decomposition at 300 ° C. or lower, hydrogen gas and carbon fumes are generated by thermal decomposition immediately after being introduced into the furnace. These thermal decomposition products do not burn in a furnace with a low oxygen concentration, but burn with being mixed with free air near the converter exhaust gas hood,
The converter exhaust gas hood is heated to a high temperature to promote wear of the exhaust gas hood.
【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。Further, a part of the organic matter volatilized from the organic insulator (synthetic resin) in the scrap is not completely decomposed and burned, and is absorbed and colored by the sulfuric acid product manufactured from the converter exhaust gas as a raw material. I have a problem.
【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。An object of the present invention is to establish a new industrial recycling method which replaces converter processing of scraps.
【0010】[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。[Means for Solving the Problems] Generally speaking, the method of directly treating in the copper smelting process requires almost no pretreatment, so the treatment cost is low, and even if the content rate of valuable metals in scrap is low, the recovery rate and Since there is no problem in large-scale processing, it is desirable as a recycling method. Therefore, in order to solve the problems such as exhaust gas hood wear and coloring of the product sulfuric acid due to the converter treatment, the present inventor has conceived to treat scraps in a copper ore smelting flash furnace. . Unlike a converter, in a closed-type flash smelting furnace, organic substances that have volatilized from organic insulators (synthetic resins) in scrap are completely decomposed and burned, so that coloring of the product sulfuric acid can be avoided.
【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。On the other hand, even in the method of processing in a flash furnace,
A new problem arises when processing scrap containing a small amount of valuable metal and containing a large amount of synthetic resin and inorganic insulator (glass fiber, etc.). That is, in the flash furnace, the oxygen concentration directly above the melt is extremely low, so even if it is simply charged from the settler section of the flash furnace, the oxygen concentration in the atmosphere is low, so it will not completely burn and the melt surface (on top of the slag) There is a problem that it will surface. Further, since the stirring effect of the molten metal in the flash smelting furnace is smaller than that in the converter, the pyrolysis residue and the inorganic insulator in the scrap do not form slag. Therefore, the transfer (sedimentation) of valuable metal in scrap to the mat is prevented. Also, when a large amount is input from the settler section, the organic substances generated from synthetic resins are introduced to the boiler together with the exhaust gas of the flash furnace, burned in the boiler, and the temperature inside the boiler is raised, so that the boiler of the flash furnace dust is heated. Induces fusion to the water tube.
【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。In order to realize the treatment of scraps in the flash smelting furnace, it is necessary to overcome these problems. As a result of repeated research, the inventors of the present invention can solve these problems and put the scraps into practical use by throwing them into the shaft ceiling of the flash furnace. Found. Thus, the present invention is characterized in that scraps containing valuable metals are charged into a copper ore smelting flash smelting furnace from the shaft ceiling, and valuable metals are recovered to a mat that remains in the furnace. Provide a method of recycling valuable metals from. Most practically, the scraps are crushed in advance, mixed with the charge for smelting copper ore and charged into the furnace from the flash smelting furnace burner.
【0013】[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。BEST MODE FOR CARRYING OUT THE INVENTION As shown in FIG. 1, a flash smelting furnace for smelting copper ore comprises a shaft 1, a setler 2 and an uptake 3. The book concentrate burner 5 is equipped. A copper ore smelting charge is generally blown from a concentrate burner together with a fine powder concentrate together with a solvent (flux) together with oxygen-enriched air or oxygen or high-temperature hot air to cause an instantaneous oxidation reaction.
Since the amount of heat is insufficient only with the heat of oxidation reaction, heavy oil is usually assisted from the concentrate burner. While falling through the shaft,
The concentrate melts at a high temperature of 1300 ° C. or higher, and is separated by a setler into a mat (kawa, sulfide melt) containing 50 to 68% of copper and a slag (karami) floating above it. A slag 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 auxiliary equipment. After recovering heat in the boiler, the cooled exhaust gas collects dust with an electric dust collector and is then sent to a sulfuric acid factory to produce sulfuric acid.
【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。According to the present invention, as a method of recycling valuable metals from scraps, scraps containing valuable metals are charged from the ceiling part 4 of the shaft 1 into the self-melting furnace for smelting copper ore, and valuable metals are charged. The feature is that metal is collected in a mat (sulfide melt) that stays in the furnace. Although a charging port for scraps may be separately provided in the ceiling, scraps are crushed in advance and mixed with copper ore concentrate and a solvent to be loaded into the furnace from the flash smelting furnace burner 5. It is preferable to enter. In particular, for scraps that are flame-retardant and flame-melting, 40 mm or less, preferably 1
Crushed to 0 mm or less, more preferably 2 mm or less,
It is charged into the furnace with ore from the flash furnace concentrate burner.
The scraps may be crushed by using an appropriate crushing mill, but it is convenient to crush the solvent (silica) for the flash smelting furnace at the same time, and the cost hardly increases.
【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。As a result, the scrap burns and melts with the ore at a high temperature of 1300 ° C. or higher while the shaft is falling, and the valuable metal is quickly absorbed by the mat after reaching the molten metal. In addition, incombustibles such as SiO 2 in scrap are quickly absorbed by the slag. At this time, some valuable metals are
It is thought that it becomes an oxide while the shaft falls, but it is reduced (sulfided) by iron sulfide supplied from molten ore particles,
Absorbed by matte (sulfide phase).
【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。Further, in this method, since the scrap is evenly dispersed in a wide range of the molten metal just below the shaft, even if there is scrap with a slight delay in combustion and melting during the fall of the shaft, it will be in one place of the settler section. It is easier to melt after reaching the molten metal and to slag unnecessary parts, as compared to the case of intensive injection. Further, since the organic substances generated by thermal decomposition from the synthetic resins in the scrap are completely decomposed and oxidized while passing through the flash furnace, they are not burned in the boiler. When a halogen element such as chlorine or fluorine is contained in the organic insulator, it can be removed in the pretreatment step of the sulfuric acid manufacturing process.
【0017】[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。[Example] An operation was carried out in which scrap mainly consisting of electric component scrap was crushed and charged into a flash furnace. (I) Scrap before crushing The particle size of the scrap before crushing is mainly about 80 mm at maximum and about 20 mm at minimum, and many substrates and copper wire cords were also included. The average component analysis values for the entire processed scrap are shown in Table 1 below. Since it also contains an inorganic insulator, it has a high SiO 2 content.
【0018】[0018]
【表1】 [Table 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。(Ii) Grinding Method and Grinding Particle Size Grinding was carried out together with silica using a ball mill for grinding silica stone which is usually used as a solvent (flux) for a flash furnace. Table 2 shows the particle size distribution of scrap after crushing.
【0020】[0020]
【表2】 [Table 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(Iii) Charging into the flash furnace The scrap is mixed with silica during crushing. This scrap is further mixed with copper ore and then dried, and then it is put on the ceiling of the flash furnace shaft. The furnace was charged from the installed concentrate burner. The ore and scrap charging rates were as follows: Ore charging: 65 Ton / Hr Scrap charging: 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。(Iv) Recovery of valuables The valuable metals charged in the flash furnace are absorbed by the mat and sent to the converter in the next step, but the amount contained in the slag and discharged is lost. Becomes FIG. 2 shows the copper content in the flash slag during the test period. It can be seen that the copper content in the slag during the test period did not differ from normal operation, and the copper in the scrap was absorbed by the mat without loss.
【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。Gold and silver are also collected in the mat, like copper. Figure 3 shows the matte gold during the test period,
The change of silver content is shown. As can be seen from FIG. 3, the gold and silver contents in the mat increased with the start of the test operation, indicating that gold and silver had been collected in the mat.
【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。Next, in order to investigate the recovery rate of valuable metals to the mat, the loss rate of silver to the slag is evaluated. Most of the loss of silver to the slag is contained in the suspended matte particles in the molten slag, so it is evaluated in consideration of the increase in the silver content in the matte due to scrap charging. There is a need. Therefore, it is appropriate to evaluate by the distribution coefficient between slag / mat (= content in slag / content in mat). Figure 4 shows changes in the distribution coefficient of silver during the test period.
Shown in As can be seen from Fig. 4, the distribution coefficient of silver is not different from that during normal operation. From this, it can be judged that the recovery rate of silver in the scrap into the mat was equal to the recovery rate from the ore during normal operation (99% or more).
【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。(V) Coloring of product sulfuric acid and influence on boiler temperature Furthermore, as a result of examining the degree of coloring of product sulfuric acid and the rise in boiler temperature, it was found that the self-melting of scrap due to the operation of the flash-charging furnace charging test operation. Product sulfuric acid produced from furnace exhaust gas as a raw material was not colored. It is considered that the organic insulator contained in the scrap had completely decomposed and burned. The boiler temperature did not rise due to the operation of the scrap flash furnace charging test operation. Thermal decomposition and combustion of scrap had been completed in the flash furnace shaft and settler section.
【0026】[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。According to the present invention, since scrap processing is combined with copper smelting in a copper smelting flash smelting furnace, valuable metals can be recovered at low cost even from scraps having a low valuable metal content. . In the case of flame-retardant scraps, it must be crushed in advance, but since this crushing can be performed at the same time as the crushing of the solvent (silica) for the flash furnace, there is almost no cost increase. Further, since the organic insulator can be reliably pyrolyzed 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 manufacturing process. Further, since halogen elements such as chlorine and fluorine contained in the organic insulator can be removed in the pretreatment stage of the sulfuric acid manufacturing process, it is not necessary to newly provide a gas treatment facility for pollution prevention. It is virtually unnecessary to repair the copper smelting flash furnace itself or change the operating conditions. As described above, the conventional method does not match the treatment cost and can be applied to industrial waste that is difficult to be finally disposed of. Therefore, it is useful not only for resource saving but also for environmental protection.
【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。FIG. 1 is a schematic view of a flash smelting furnace for copper ore smelting and a waste heat boiler.
【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。FIG. 2 is a graph showing the copper content in the flash slag during the test period.
【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。FIG. 3 is a graph showing changes in the gold and silver contents of the mat during the test period.
【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。FIG. 4 is a graph showing changes in the distribution coefficient of silver during the test period.
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 1 Shaft 2 Setler 3 Uptake 4 Ceiling 5 Concentrate burner 6 Waste heat boiler
Claims (2)
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。1. A scrap which is characterized in that scraps containing valuable metals are loaded into a flash ore smelting furnace for copper ore smelting from the shaft ceiling, and valuable metals are recovered to a mat that remains in the furnace. Method for recycling valuable metals.
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を特徴とする請求項1のスクラッ
プ類からの有価金属のリサイクル方法。2. The scraps are crushed in advance, and the scraps are mixed with a copper ore smelting charge and charged into the furnace from a flash smelting furnace concentrate burner. A method of recycling valuable metals from scraps.
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP25829695A JP3535629B2 (en) | 1995-09-12 | 1995-09-12 | Recycling of valuable metals from scraps |
KR1019960031589A KR100311653B1 (en) | 1995-09-12 | 1996-07-30 | Recycling of Valuable Metals from Scraps |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP25829695A JP3535629B2 (en) | 1995-09-12 | 1995-09-12 | Recycling of valuable metals from scraps |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0978151A true JPH0978151A (en) | 1997-03-25 |
JP3535629B2 JP3535629B2 (en) | 2004-06-07 |
Family
ID=17318295
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP25829695A Expired - Lifetime JP3535629B2 (en) | 1995-09-12 | 1995-09-12 | Recycling of valuable metals from scraps |
Country Status (2)
Country | Link |
---|---|
JP (1) | JP3535629B2 (en) |
KR (1) | KR100311653B1 (en) |
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-
1995
- 1995-09-12 JP JP25829695A patent/JP3535629B2/en not_active Expired - Lifetime
-
1996
- 1996-07-30 KR KR1019960031589A patent/KR100311653B1/en not_active Expired - Fee Related
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WO2022224478A1 (en) | 2021-04-21 | 2022-10-27 | Jx金属株式会社 | Electrical and electronic component scrap processing method, and electrical and electronic component scrap processing device |
WO2024135143A1 (en) | 2022-12-20 | 2024-06-27 | Jx金属株式会社 | Method for treating objects to be treated including massive copper wire scrap |
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