JPH0625763A - Treatment of intermediate product of smelting - Google Patents

Treatment of intermediate product of smelting

Info

Publication number
JPH0625763A
JPH0625763A JP4038151A JP3815192A JPH0625763A JP H0625763 A JPH0625763 A JP H0625763A JP 4038151 A JP4038151 A JP 4038151A JP 3815192 A JP3815192 A JP 3815192A JP H0625763 A JPH0625763 A JP H0625763A
Authority
JP
Japan
Prior art keywords
copper
arsenic
smelting
intermediate product
treating
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
JP4038151A
Other languages
Japanese (ja)
Other versions
JP3052535B2 (en
Inventor
Takeyoshi Shibazaki
武義 柴崎
Nozomi Hasegawa
望 長谷川
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 JP4038151A priority Critical patent/JP3052535B2/en
Publication of JPH0625763A publication Critical patent/JPH0625763A/en
Application granted granted Critical
Publication of JP3052535B2 publication Critical patent/JP3052535B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

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

Landscapes

  • Manufacture And Refinement Of Metals (AREA)

Abstract

PURPOSE:To enable the economical treatment of the intermediate product of smelting by sending a leaching liquid to a neutralizing stage, adjusting this liquid to specific pH and integrally settling and separating arsenic and copper. CONSTITUTION:The intermediate product of smelting consisting of acid soluble metal groups contg. at least the arsenic and cadmium and the copper is subjected to a leaching treatment with the acidity of sulfuric acid. The leaching liquid obtd. in such a manner is sent to a neutralizing stage and is adjusted to >=4.5 and <=6pH, by which the arsenic and copper are integrally settled and separated. The amt. of the arsenic contained in the liquid to be subjected to the neutralization treatment is specified to a range of (molar number of the arsenic) <=1/2 (molar number of the copper)+(molar number of iron). Hydrogen sulfide, sodium hydrogensulfide or zinc powder is added to the liquid obtd. after the settlement and sepn. of the arsenic and copper, by which the cadmium is settled and separated. As a result, the copper is economically recovered.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、銅製錬の際に生じる煙
灰や、鉛製錬の際に生じる含銅ドロスなどの製錬中間産
物を処理する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method of treating smelting intermediate products such as smoke ash generated during copper smelting and copper-containing dross generated during lead smelting.

【0002】[0002]

【従来の技術と発明が解決しようとする課題】銅を製錬
する際には、銅の他に鉛、ビスマス、亜鉛、ヒ素、カド
ミウム等の不純物を含む煙灰が製錬中間産物として生じ
る。また鉛を製錬する際には、鉛の他に不純物としての
銅および場合によってはカドミウム、亜鉛、ヒ素等を含
む含銅ドロスが製錬中間産物として生じる。これら製錬
中間産物は、目的とする成分以外の成分、すなわち不純
物を系内から取り除くために、その一部または全部が主
工程から抜き出される。そして、各成分に分離して回収
した後有効利用される。
2. Description of the Related Art When smelting copper, smoke ash containing impurities such as lead, bismuth, zinc, arsenic and cadmium in addition to copper is produced as a smelting intermediate product. Further, when smelting lead, copper as an impurity in addition to lead and, in some cases, copper-containing dross containing cadmium, zinc, arsenic, etc. are produced as a smelting intermediate product. Some or all of these smelting intermediate products are extracted from the main process in order to remove components other than the intended components, that is, impurities from the system. Then, after being separated into each component and collected, it is effectively used.

【0003】例えば、銅製錬時に発生する煙灰、すなわ
ち銅の他に鉛、ビスマス、亜鉛、ヒ素、カドミウム等の
不純物を含む製錬中間産物は図3に示すように処理され
ていた。まず硫酸酸性で銅、ヒ素、亜鉛、カドミウム等
の酸溶性金属を浸出して、浸出滓と分離する(浸出工程
1)。浸出滓には鉛、ビスマス、アンチモン等が含まれ
ている。この鉛を含む浸出滓は、鉛製錬原料とされる。
ついで浸出液は、下記の処理方法のうち適宜な方法で処
理されている。 先ず、浸出液に硫酸鉄または塩化鉄を加えてヒ素を
酸化しつつ中和し、ヒ素をヒ酸鉄として除去する(酸化
・中和工程2)。除去されたヒ酸鉄は銅製錬の溶錬工程
に送られて処理される。ヒ酸鉄が除去された母液には、
亜鉛末を添加して亜鉛末セメンテーションにより銅、カ
ドミウムを別々に順次分離する(セメンテーション工程
3)。この後母液を濃縮または中和して亜鉛を回収する
(濃縮/中和工程4)。 前記の酸化・中和工程2でヒ素を除去した後、母
液に亜鉛末を添加して銅のみを亜鉛末セメンテーション
で分離し(セメンテーション工程5)、この母液を濃縮
又は中和して亜鉛とカドミウムを同時に回収する(濃縮
/中和工程6)。 浸出液中のヒ素の含有量が多い場合は、浸出液にH
2S、NaHS等を添加してヒ素を硫化物として除去
(硫化工程7)した後、前記またはの処理を行うこ
ともある。
For example, smoke ash generated during copper smelting, that is, a smelting intermediate product containing impurities such as lead, bismuth, zinc, arsenic and cadmium in addition to copper has been treated as shown in FIG. First, acid-soluble metals such as copper, arsenic, zinc and cadmium are leached with sulfuric acid to separate them from the leaching slag (leaching step 1). The leachate contains lead, bismuth, antimony, etc. The lead-containing leach slag is used as a lead smelting raw material.
Next, the leachate is treated by an appropriate method among the following treatment methods. First, iron sulfate or iron chloride is added to the leachate to neutralize it while oxidizing arsenic to remove arsenic as iron arsenate (oxidation / neutralization step 2). The removed iron arsenate is sent to the smelting process of copper smelting for processing. In the mother liquor from which iron arsenate has been removed,
Zinc dust is added and copper and cadmium are sequentially separated by zinc dust cementation (cementation step 3). Thereafter, the mother liquor is concentrated or neutralized to recover zinc (concentration / neutralization step 4). After removing arsenic in the above-mentioned oxidation / neutralization step 2, zinc powder is added to the mother liquor to separate only copper by zinc powder cementation (cementation step 5), and the mother liquor is concentrated or neutralized to obtain zinc. And cadmium are simultaneously recovered (concentration / neutralization step 6). If the leaching solution contains a large amount of arsenic, H
After the addition of 2 S, NaHS or the like to remove arsenic as a sulfide (sulfurization step 7), the treatment described above or may be performed.

【0004】なお、上述のようにして回収された銅、ヒ
素は、通常、銅製錬工程に送られ、亜鉛、カドミウムは
亜鉛製錬工程に送られる。
The copper and arsenic recovered as described above are usually sent to a copper smelting process, and zinc and cadmium are sent to a zinc smelting process.

【0005】前記のような銅製錬煙灰の処理方法には、
次のような問題があった。 浸出液からヒ素を取り除くために比較的高価な鉄試
薬または硫化剤を使用しているので、処理コストが高
い。 浸出液からヒ素を除去するために鉄試薬を用いた場
合は、添加した鉄試薬の分、沈澱量が増えるので、この
沈澱物の処理に多額の費用がかかる。 浸出液からヒ素を除去するために硫化剤を用いた場
合は、ヒ素の硫化物の脱水性が著しく悪いので、やはり
沈澱物量が多くなる。 上記の処理方法は、煙灰中の銅濃度が低く亜鉛濃度
が高い場合には有利である。しかし、逆に銅濃度が高く
亜鉛濃度が低い場合には、浸出液から銅を分離回収する
際に多量の亜鉛末が必要となるうえ、ここで用いた亜鉛
を母液を濃縮して回収する際に多大のエネルギーが必要
となる点で、経済的に不利となる。
The method for treating copper smelting smoke ash as described above includes
There were the following problems. Treatment costs are high due to the use of relatively expensive iron reagents or sulfiding agents to remove arsenic from the leachate. When an iron reagent is used to remove arsenic from the leachate, the amount of the added iron reagent increases the amount of precipitation, and thus the treatment of the precipitate is expensive. When a sulfiding agent is used to remove arsenic from the leachate, the amount of precipitate is also large because the dehydration property of arsenic sulfide is extremely poor. The above treatment method is advantageous when the concentration of copper in the smoke ash is low and the concentration of zinc is high. However, on the contrary, when the copper concentration is high and the zinc concentration is low, a large amount of zinc powder is required when separating and recovering copper from the leachate, and the zinc used here is recovered when the mother liquor is concentrated and recovered. It is economically disadvantageous in that it requires a large amount of energy.

【0006】次に鉛製錬時に生じる銅と鉛を主成分とす
る製錬中間産物、すなわち含銅ドロスの処理方法を説明
する。含銅ドロスは、従来、ショートロータリーファー
ネス又は電気炉等で溶解処理して、銅カワと粗鉛とに分
離する乾式処理により処理されていた。ところがこの処
理方法では、銅カワ中に相当量の鉛が混入するので、鉛
ロスを招くと共に、銅製錬にとって有害な鉛が銅製錬工
程に持ち込まれてしまう問題があった。
Next, a method for treating a smelting intermediate product containing copper and lead as main components, which is produced during lead smelting, that is, a copper-containing dross will be described. Conventionally, copper-containing dross has been processed by a dry process in which it is dissolved in a short rotary furnace, an electric furnace or the like, and separated into copper river and crude lead. However, in this treatment method, since a considerable amount of lead is mixed into the copper river, there is a problem that lead loss is caused and lead harmful to copper smelting is brought into the copper smelting process.

【0007】そこで最近では、含銅ドロスから硫酸また
はアンモニアを用いて銅を浸出し、得られた浸出液から
溶媒抽出・電解採取することによって(以下、SX/E
X法と記す)直接電気銅を回収する例が多い。しかしこ
の処理方法では、鉛製錬に用いた原料に銅と共にカドミ
ウム、亜鉛、ヒ素等の硫酸またはアンモニアに可溶な成
分が含まれている場合には、これらが浸出液中に蓄積し
て来るので、結局前記銅製錬煙灰を処理したのと同様の
方法でこれらを取り除く処理を行なう必要が生じて経済
的に不利である。また含銅ドロスのような製錬中間産物
を原料にしてSX/EX法を実施すると、生産規模が、
経済的に製造できる規模の1/10程度となり、この点
でもこの含銅ドロスの処理方法は経済的に不利である。
さらに電解採取は電解精製に比較して約10倍の電気エ
ネルギーを要するので、この含銅ドロスの処理方法は原
理的にも不利である。
Therefore, recently, copper is leached from the copper-containing dross using sulfuric acid or ammonia, and solvent extraction and electrowinning are performed from the obtained leachate (hereinafter referred to as SX / E).
In many cases, electrolytic copper is directly recovered. However, in this treatment method, when the raw material used for lead smelting contains components soluble in sulfuric acid or ammonia such as cadmium, zinc, and arsenic as well as copper, these will accumulate in the leachate. In the end, it is necessary to perform a treatment for removing the copper smelting ash by the same method as that for treating the copper smelting ash, which is economically disadvantageous. When the SX / EX method is carried out using a smelting intermediate product such as copper-containing dross as a raw material, the production scale is
It is about 1/10 of the economically manufacturable scale, and this is also an economically disadvantageous treatment method for copper-containing dross.
Further, electrolytic extraction requires about 10 times as much electric energy as electrolytic refining, and thus this method of treating copper-containing dross is disadvantageous in principle.

【0008】本発明は前記事情に鑑みてなされたもの
で、銅と共にヒ素、カドミウム等の酸溶性金属を含む製
錬中間産物、特に、銅を多量に含む製錬中間産物を経済
的に処理できる方法を提供することを目的とする。
The present invention has been made in view of the above circumstances, and can economically process a smelting intermediate product containing an acid-soluble metal such as arsenic and cadmium together with copper, particularly a smelting intermediate product containing a large amount of copper. The purpose is to provide a method.

【0009】[0009]

【課題を解決するための手段】本発明の製錬中間産物の
処理方法では、製錬中間産物を硫酸酸性で浸出処理し、
こうして得られた浸出液を中和工程に送りpH4.5以
上6以下に調整してヒ素および銅を一括して沈澱させ分
離することによって前記課題を解決した。中和工程のp
Hが4.5未満になると、ヒ素が液中に残存する。また
pHが5を越えると浸出液中のカドミウム(亜鉛が含ま
れている場合は、亜鉛も)が水酸化物となって、ヒ素お
よび銅と共に沈澱して来るので、沈澱物を銅製錬用原料
にそのまま利用できなくなる問題が生じる。
In the method for treating a smelting intermediate product of the present invention, the smelting intermediate product is leached with sulfuric acid acidity,
The leachate thus obtained was sent to the neutralization step to adjust the pH to 4.5 or more and 6 or less, and the arsenic and copper were collectively precipitated and separated to solve the above problems. P in the neutralization step
When H is less than 4.5, arsenic remains in the liquid. If the pH exceeds 5, cadmium (and zinc, if zinc is contained) in the leachate will become hydroxide and precipitate with arsenic and copper. The precipitate is used as a raw material for copper smelting. There is a problem that it cannot be used as it is.

【0010】前記中和工程の対象となる液に含まれてい
るヒ素の量は、下記(I)式で示される範囲であること
が望ましい。 (ヒ素のモル数) ≦ 1/2(銅のモル数)+(鉄のモル数) …………(I) 浸出漬液中のヒ素の量がこの範囲から外れていた場合
は、浸出液に銅や鉄を添加して、上記条件を満たすよう
にすることもできる。本発明の製錬中間産物の処理方法
で得られるヒ素および銅を沈澱分離したあとの液(以
下、中和工程の濾液と記す)の処理法としては、同中和
工程の濾液に硫化水素、硫化水素ナトリウム又は亜鉛末
を加えてカドミウムを沈澱分離する方法や、同濾液に水
酸化ナトリウム等を加えpHを上げてカドミウムを水酸
化物として沈澱分離する方法を採用できる。後述した方
法の場合では、浸出液に亜鉛が含まれていた場合、この
亜鉛もカドミウムと同時に沈澱分離される。本発明の処
理方法の対象となる製錬中間産物としては、銅製錬時に
発生する煙灰(銅製錬煙灰)や鉛製錬時に発生する含銅
ドロスを例示できる。
The amount of arsenic contained in the liquid to be subjected to the neutralization step is preferably in the range represented by the following formula (I). (Mole number of arsenic) ≤ 1/2 (Mole number of copper) + (Mole number of iron) (I) If the amount of arsenic in the leachate is out of this range, the leachate contains copper. It is also possible to add iron or iron to satisfy the above conditions. As a method for treating the liquid (hereinafter referred to as the filtrate of the neutralization step) obtained by the precipitation and separation of arsenic and copper obtained by the method of treating the smelting intermediate product of the present invention, hydrogen sulfide, A method in which sodium hydrogen sulfide or zinc powder is added to precipitate and separate cadmium, and a method in which sodium hydroxide or the like is added to the filtrate to raise the pH and precipitate and separate cadmium as hydroxide can be adopted. In the case of the method described below, when zinc is contained in the leachate, this zinc is also precipitated and separated simultaneously with cadmium. Examples of the smelting intermediate product that is the target of the treatment method of the present invention include smoke ash generated during copper smelting (copper smelting smoke ash) and copper-containing dross generated during lead smelting.

【0011】(発明の具体的説明1)次に、図を参照し
て、本発明の製錬中間産物の処理方法を更に具体的に説
明する。図1は請求項3の処理方法の一例を示すフロー
チャートである。この処理方法では、酸溶性金属である
ヒ素、カドミウム、亜鉛と、酸不溶性金属である鉛、ビ
スマス、アンチモンと、銅とを含む銅製錬煙灰または含
銅ドロスが処理できる。この処理方法では、まず製錬中
間産物に硫酸を加えて、空気または酸素を吹き込みつ
つ、銅、ヒ素等の浸出処理を行い(浸出工程S1)、不
溶性の鉛、ビスマス、アンチモンを浸出滓として分離す
る。この浸出滓は鉛製錬工程に送られる。他方浸出液に
は炭酸カルシウムあるいは水酸化カルシウムを添加して
pHを4.5〜6に調整する中和処理を行う(中和工程
S2)。pHをこの範囲に調整すると、ヒ素および銅が
同時に沈澱するのでこれを分離する。この中和工程で生
じた残滓は銅製錬工程に送られる。次に前記中和工程の
濾液に、硫化水素、硫化水素ナトリウムあるいは亜鉛末
を加える。すると母液に含まれているカドミウムが硫化
あるいは亜鉛末セメンテーションされて沈澱分離される
(Cd除去工程S3)。この後カドミウムが除去された
母液のpHを上げる(pH調整工程S4)。この処理方
法のpH調整工程S4では、水酸化カルシウムを用いて
pH5〜9にすると良い。このようにすると水酸化物と
なった状態で亜鉛が除去される。
(Detailed Description 1 of the Invention) Next, the method for treating a smelting intermediate product of the present invention will be described more specifically with reference to the drawings. FIG. 1 is a flowchart showing an example of the processing method of claim 3. In this treatment method, copper smelting ash or copper-containing dross containing acid-soluble metals such as arsenic, cadmium and zinc and acid-insoluble metals such as lead, bismuth, antimony and copper can be treated. In this treatment method, sulfuric acid is first added to the smelting intermediate product, and leaching treatment of copper, arsenic, etc. is performed while blowing air or oxygen (leaching step S1), and insoluble lead, bismuth, and antimony are separated as leaching sludge. To do. This leach slag is sent to the lead smelting process. On the other hand, calcium carbonate or calcium hydroxide is added to the leachate to perform a neutralization treatment for adjusting the pH to 4.5 to 6 (neutralization step S2). When the pH is adjusted to this range, arsenic and copper are simultaneously precipitated and separated. The residue produced in this neutralization process is sent to the copper smelting process. Next, hydrogen sulfide, sodium hydrogen sulfide or zinc dust is added to the filtrate of the neutralization step. Then, the cadmium contained in the mother liquor is sulfided or zinc dust cemented and precipitated and separated (Cd removing step S3). After this, the pH of the mother liquor from which cadmium has been removed is raised (pH adjusting step S4). In the pH adjusting step S4 of this processing method, it is advisable to adjust the pH to 5 to 9 using calcium hydroxide. In this way, zinc is removed in the state of being hydroxide.

【0012】この処理方法によると、銅がヒ酸銅と水酸
化銅の混合物として回収される。この混合物は、銅製錬
原料に利用できる。従来の処理方法で回収されたヒ素を
含む残滓は一般に銅製錬の溶錬工程で処理されていたの
で、前記ヒ酸銅を溶錬工程で処理しても何等問題ない。
加えて前記銅を含む混合物を銅製錬工程で処理した場合
は、前記従来の処理方法で述べたSX/EW法で銅を回
収する場合に比較して安価に処理できる。また銅回収の
為だけにSX/EW法用設備を設けたり人員を配置する
必要が無くなる点でも有利である。
According to this treatment method, copper is recovered as a mixture of copper arsenate and copper hydroxide. This mixture can be used as a raw material for copper smelting. Since the arsenic-containing residue recovered by the conventional treatment method is generally treated in the smelting step of copper smelting, there is no problem in treating the copper arsenate in the smelting step.
In addition, when the mixture containing copper is treated in the copper smelting step, it can be treated at a lower cost than when copper is recovered by the SX / EW method described in the conventional treatment method. It is also advantageous in that it is not necessary to provide equipment for the SX / EW method or to arrange personnel only for copper recovery.

【0013】(発明の具体的説明2)図2は請求項4の
処理方法の一例を示すものである。この処理方法では、
図1に示した方法と同様に製錬中間産物を浸出工程S1
と中和工程S2で処理した後、直ちにpH調整工程S5
(以下、(変形)pH調整工程S5と記す)を行う。こ
の処理方法の(変形)pH調整工程S5では、水酸化ナ
トリウムを用いてpHを5〜9に上げると良い。このよ
うにすると亜鉛とカドミウムが水酸化物となり混合状態
で沈澱する。
(Detailed Description 2 of the Invention) FIG. 2 shows an example of the processing method of claim 4. With this processing method,
As in the method shown in FIG. 1, a smelting intermediate product leaching step S1
And the neutralization step S2, immediately after the pH adjustment step S5
(Hereinafter, referred to as (deformed) pH adjusting step S5). In the (deformed) pH adjusting step S5 of this treatment method, it is preferable to raise the pH to 5 to 9 using sodium hydroxide. By doing so, zinc and cadmium become hydroxides and precipitate in a mixed state.

【0014】[0014]

【作用】本発明の処理方法では、少なくともヒ素および
カドミウムを含む酸溶性金属群と銅とからなる製錬中間
産物を硫酸酸性で浸出処理し、こうして得られた浸出液
を中和工程に送りpH4.5以上6以下に調整する。こ
のようにすると銅とヒ素とが複塩を生成して沈澱除去さ
れる(中和工程の対象となる液に鉄や亜鉛が含まれてい
る場合には、ヒ素はこれらとも複塩を生成して除去され
る)。このようにこの処理方法によれば、ヒ素を銅と共
に沈澱し除去するので、処理工程が簡略となるうえ、従
来法のようにヒ素を除去するためにのみ高価な鉄試薬ま
たは硫化剤を使用する必要がない。しかもこれら薬品の
使用に伴う沈澱物処理費用の増大も回避できる。よって
この処理方法によれば、銅と共にヒ素、カドミウム等の
酸溶性金属を含む製錬中間産物を経済的に処理できる。
またこの処理方法では、亜鉛末を用いずに、pH4.5
〜6とする中和工程S2で銅の回収を行うので、銅濃度
が高く亜鉛濃度が低い製錬中間産物を処理する場合でも
経済的に銅回収を行うことができる。
In the treatment method of the present invention, the smelting intermediate product consisting of the acid-soluble metal group containing at least arsenic and cadmium and copper is leached with sulfuric acid, and the leachate thus obtained is sent to the neutralization step to have a pH of 4. Adjust to 5 or more and 6 or less. By doing this, copper and arsenic form a double salt and are precipitated and removed (if the liquid to be neutralized contains iron or zinc, arsenic also forms a double salt. Removed). As described above, according to this treatment method, arsenic is precipitated and removed together with copper, which simplifies the treatment process and uses an expensive iron reagent or sulfidizing agent only for removing arsenic as in the conventional method. No need. In addition, it is possible to avoid an increase in the cost for treating the precipitate due to the use of these chemicals. Therefore, according to this treatment method, a smelting intermediate product containing an acid-soluble metal such as arsenic and cadmium together with copper can be treated economically.
Moreover, in this treatment method, without using zinc dust,
Since copper is recovered in the neutralization step S2 of ~ 6, copper can be recovered economically even when processing a smelting intermediate product having a high copper concentration and a low zinc concentration.

【0015】また請求項2の処理方法では、中和工程の
対象となる液に含まれているヒ素のモル数が(銅のモル
数)の半分と(鉄のモル数)との和以下なので、浸出液
中に含まれている3価のヒ素を中和工程でCu(AsO
22、FeAsO4・2H2Oの複塩の形にしてほぼ完全
に沈澱除去できる。ヒ素が母液中に残留すると、Cd除
去工程S3でカドミウムを亜鉛末セメンテーションする
際にアルシンが生成する恐れがあり望ましくないが、こ
の処理方法によればそのような恐れを回避できる。また
(変形)pH調整工程S5でカドミウムと亜鉛とを水酸
化物として同時に除去する場合でも、ヒ素が残留してい
ると排水処理の負荷が高くなる不都合を生じるが、この
処理方法によればこの不都合も回避できる。
Further, in the treatment method of claim 2, since the number of moles of arsenic contained in the liquid to be neutralized is less than the sum of half of (the number of moles of copper) and (the number of moles of iron). , Trivalent arsenic contained in the leachate is Cu (AsO
2 ) 2 , FeAsO 4 .2H 2 O can be almost completely precipitated and removed in the form of a double salt. If arsenic remains in the mother liquor, arsine may be generated when cadmium is subjected to zinc powder cementation in the Cd removing step S3, which is not desirable, but such a possibility can be avoided by this treatment method. Further, even when cadmium and zinc are simultaneously removed as hydroxides in the (deformation) pH adjusting step S5, if arsenic remains, there is a disadvantage that the load of wastewater treatment becomes high. Inconvenience can be avoided.

【0016】[0016]

【実施例】【Example】

(実施例1)図2に示した処理方法で表1に示す組成の銅
製錬煙灰60トンを処理した。まずこの銅製錬煙灰に硫
酸プラントの廃酸240m3(H2SO4 50g/リット
ル)を加えてパルプ化した後、濃硫酸14.7トンを加
え、空気を1Nm3/minで吹き込みながら、50℃
で1時間浸出処理した(浸出処理工程S1)。このあと
フィルタープレスにより浸出滓を濾別した。ついで浸出
液に30%炭酸カルシウムスラリーを加えてpH5.1
に調整し30分保持した(中和工程S2)。ついでこの
液を遠心分離機にかけて残滓を濾別した。次に中和工程
S2で得られた濾液に50%NaOH液を加えてpH8
とし、1時間放置した((変形)pH調整工程S5)。
ついでこの液をフィルタプレスにかけて、残滓と濾液に
分けた。濾液は280m3であった。この濾液は、不純
物をほとんど含有せずそのまま放流できるものであっ
た。各工程で発生した物あるいは使用した物の量、およ
びそれらに含まれていた金属成分の割合を表1に示す。
(Example 1) 60 tons of copper smelting smoke ash having the composition shown in Table 1 was treated by the treatment method shown in FIG. First, 240 m 3 of waste acid from a sulfuric acid plant (50 g / l of H 2 SO 4 ) was added to this copper smelting ash to pulp, and then 14.7 tons of concentrated sulfuric acid was added, while blowing air at 1 Nm 3 / min, ℃
Was leached for 1 hour (leaching process step S1). Then, the leachate was filtered off with a filter press. Then, 30% calcium carbonate slurry was added to the leachate to adjust the pH to 5.1.
And held for 30 minutes (neutralization step S2). Then, this liquid was subjected to a centrifuge and the residue was filtered off. Next, a 50% NaOH solution is added to the filtrate obtained in the neutralization step S2 to adjust the pH to 8
And left for 1 hour ((deformation) pH adjusting step S5).
Then, this solution was subjected to a filter press to separate the residue and the filtrate. The filtrate was 280 m 3 . This filtrate contained almost no impurities and could be discharged as it was. Table 1 shows the amount of the substances generated or used in each step and the ratio of the metal components contained in them.

【0017】[0017]

【表1】 [Table 1]

【0018】表1中、中和工程の濾液の欄を見ると、炭
酸カルシウムスラリーを加えた中和工程S2で浸出液中
の銅およびヒ素をほぼ完ぺきに除去できたことが判る。
Looking at the column of the filtrate of the neutralization step in Table 1, it can be seen that the copper and arsenic in the leachate could be almost completely removed in the neutralization step S2 in which the calcium carbonate slurry was added.

【0019】(実施例2)図1に示した処理方法で、鉛製
錬から生じた含銅ドロス8.75トンと銅製錬から生じ
た煙灰10トンを処理した。これら含銅ドロスおよび煙
灰の組成は表2に示す通りであった。まず含銅ドロス
に、硫酸プラントの廃液39m3と、製錬所内で発生し
た低負荷排水23.45m3と、濃硫酸6.5トンと、
塩酸0.2トンとを加え、酸素を50Nm3/Hr吹き
込みながら、70℃で3時間浸出処理した。この後さら
に銅製錬煙灰10トンを加えて60℃でさらに浸出処理
した(浸出工程S1)。このあとフィルタープレスによ
り浸出滓を濾別した。この後浸出液に、30%炭酸カル
シウムスラリーと25%消石灰スラリーを添加してpH
5.6とし約1時間保持した(中和工程S2)。この後
この液をフィルタープレスにより濾液と残滓に濾別し
た。ついでこの濾液に亜鉛末0.11トンを添加して1
時間攪拌した(Cd除去工程S3)。この後フィルター
プレスにより濾液と残滓に濾別した。ここで生じた濾液
は、排水処理施設に返送して処理した後放流していた。
各工程で発生した物あるいは使用した物の量、およびそ
れらに含まれていた金属成分の割合を表2に示す。
Example 2 8.75 tons of copper-containing dross produced from lead smelting and 10 tons of smoke ash produced from copper smelting were treated by the treatment method shown in FIG. The compositions of these copper-containing dross and smoke ash are shown in Table 2. First the copper containing dross, and waste 39m 3 of sulfuric acid plant, the low load wastewater 23.45M 3 generated in the smelting plant, and concentrated sulfuric acid 6.5 t,
0.2 ton of hydrochloric acid was added, and leaching treatment was performed at 70 ° C. for 3 hours while blowing oxygen at 50 Nm 3 / Hr. After that, 10 tons of copper smelting ash was further added and further leached at 60 ° C. (leaching step S1). Then, the leachate was filtered off with a filter press. After this, 30% calcium carbonate slurry and 25% slaked lime slurry were added to the leachate to adjust the pH.
It was set to 5.6 and held for about 1 hour (neutralization step S2). After this, this liquid was separated into a filtrate and a residue by a filter press. Next, 0.11 ton of zinc dust was added to this filtrate to obtain 1
The mixture was stirred for an hour (Cd removal step S3). After this, the filtrate and the residue were separated by a filter press. The filtrate generated here was returned to the wastewater treatment facility for treatment and then discharged.
Table 2 shows the amounts of the substances generated or used in each step and the ratios of the metal components contained in them.

【0020】[0020]

【表2】 [Table 2]

【0021】表2の中和工程の濾液の欄を見ると、中和
工程S2で浸出液中の銅およびヒ素をほぼ完ぺきに除去
できたことが判る。
Looking at the column of the filtrate of the neutralization step in Table 2, it is found that the copper and arsenic in the leachate could be almost completely removed in the neutralization step S2.

【0022】[0022]

【発明の効果】以上説明したように本発明の処理方法で
は、少なくともヒ素およびカドミウムを含む酸溶性金属
群と銅とからなる製錬中間産物を硫酸酸性で浸出処理
し、こうして得られた浸出液を中和工程に送りpH4.
5以上6以下に調整する。このようにすると銅がヒ素と
複塩を生成して沈澱除去される(中和工程の対象となる
液に鉄や亜鉛が含まれている場合には、ヒ素はこれらと
も複塩を生成して除去される)。このようにこの処理方
法によれば、ヒ素を銅と共に沈澱し除去するので、処理
工程が簡略となるうえ、従来法のようにヒ素を除去する
ためにのみ比較的高価な鉄試薬または硫化剤を使用する
必要がない。しかもこれら薬品を使用したことに伴う沈
澱物処理費用の増大も回避できる。よってこの処理方法
によれば、銅と共にヒ素、カドミウム等の酸溶性金属を
含む製錬中間産物を経済的に処理できる。また本発明の
処理方法では、銅の回収を、亜鉛末を用いずに、pH
4.5〜6とする中和工程で行うので、銅濃度が高く亜
鉛濃度が低い製錬中間産物を処理する場合でも経済的に
銅を回収できる。また請求項2の処理方法では、中和工
程の対象となる液に含まれているヒ素のモル数が(銅の
モル数)の半分と(鉄のモル数)との和以下なので、浸
出液中に含まれている3価のヒ素を中和工程でCu(A
sO22、FeAsO4・2H2Oの複塩の形にしてほぼ
完全に沈澱除去できる。ヒ素が母液中に残留すると、カ
ドミウムを亜鉛末セメンテーションする際にアルシンが
生成する恐れがあり望ましくないが、この処理方法によ
ればそのような恐れを回避できる。またカドミウムと亜
鉛とを水酸化物として同時に除去する場合でも、ヒ素が
残留していると排水処理の負荷が高くなる不都合が生じ
るが、この処理方法によればこの不都合も回避できる。
As described above, in the treatment method of the present invention, the smelting intermediate product consisting of the acid-soluble metal group containing at least arsenic and cadmium and copper is leached with sulfuric acid, and the leachate thus obtained is treated. Send to neutralization step pH 4.
Adjust to 5 or more and 6 or less. By doing this, copper forms a double salt with arsenic and is removed by precipitation. (If iron or zinc is contained in the liquid to be neutralized, arsenic also forms a double salt. Removed). As described above, according to this treatment method, arsenic is precipitated and removed together with copper, so that the treatment process is simplified and a relatively expensive iron reagent or sulfidizing agent is used only to remove arsenic as in the conventional method. No need to use. In addition, it is possible to avoid an increase in the cost for treating the precipitate due to the use of these chemicals. Therefore, according to this treatment method, a smelting intermediate product containing an acid-soluble metal such as arsenic and cadmium together with copper can be treated economically. Further, in the treatment method of the present invention, the recovery of copper is performed without using zinc dust.
Since it is performed in the neutralization step of 4.5 to 6, copper can be economically recovered even when processing a smelting intermediate product having a high copper concentration and a low zinc concentration. In the treatment method according to claim 2, since the number of moles of arsenic contained in the liquid to be subjected to the neutralization step is equal to or less than the sum of half of (the number of moles of copper) and (the number of moles of iron), the leachate Of trivalent arsenic contained in Cu (A
It can be almost completely precipitated and removed in the form of a double salt of sO 2 ) 2 and FeAsO 4 .2H 2 O. If arsenic remains in the mother liquor, arsine may be generated during the zinc powder cementation of cadmium, which is not desirable, but this treatment method can avoid such a risk. Further, even when cadmium and zinc are simultaneously removed as hydroxides, if arsenic remains, there is a problem that the load of wastewater treatment becomes high, but this process method can also avoid this problem.

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

【図1】本発明の製錬中間産物の処理方法の1例を示す
フローチャート。
FIG. 1 is a flowchart showing an example of a method for treating a smelting intermediate product according to the present invention.

【図2】本発明の製錬中間産物の処理方法の他の例を示
すフローチャート。
FIG. 2 is a flowchart showing another example of the method for treating a smelting intermediate product of the present invention.

【図3】従来の製錬中間産物の処理方法を示すフローチ
ャート。
FIG. 3 is a flowchart showing a conventional method for treating a smelting intermediate product.

【符号の説明】[Explanation of symbols]

S1 浸出工程 S2 中和工程 S3 Cd除去工程 S4 pH調整工程 S5 (変形)pH調整工程 S1 Leaching step S2 Neutralizing step S3 Cd removing step S4 pH adjusting step S5 (deformation) pH adjusting step

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 少なくともヒ素およびカドミウムを含む
酸溶性金属群と銅とからなる製錬中間産物を硫酸酸性で
浸出処理し、こうして得られた浸出液を中和工程に送り
pH4.5以上6以下に調整してヒ素および銅を一括し
て沈澱させ分離することを特徴とする製錬中間産物の処
理方法。
1. A smelting intermediate product consisting of an acid-soluble metal group containing at least arsenic and cadmium and copper is leached with sulfuric acid, and the leachate thus obtained is sent to a neutralization step to a pH of 4.5 or more and 6 or less. A method for treating a smelting intermediate product, which comprises adjusting and precipitating and separating arsenic and copper all together.
【請求項2】 前記中和工程の対象となる液に含まれて
いるヒ素の量が、 (ヒ素のモル数) ≦ 1/2(銅のモル数)+(鉄のモル
数) の範囲にあることを特徴とする請求項1記載の製錬中間
産物の処理方法。
2. The amount of arsenic contained in the liquid to be neutralized is within the range of (the number of arsenic moles) ≦ 1/2 (the number of moles of copper) + (the number of moles of iron). The method for treating a smelting intermediate product according to claim 1, wherein
【請求項3】 請求項1の製錬中間産物の処理方法にお
いて、ヒ素および銅を沈澱分離して得られた液に、硫化
水素、硫化水素ナトリウム又は亜鉛末を加えてカドミウ
ムを沈澱分離することを特徴とする製錬中間産物の処理
方法。
3. The method for treating a smelting intermediate product according to claim 1, wherein hydrogen sulfide, sodium hydrogen sulfide or zinc powder is added to a liquid obtained by separating arsenic and copper by precipitation to separate cadmium by precipitation. A method for treating a smelting intermediate product characterized by the above.
【請求項4】 請求項1の製錬中間産物の処理方法にお
いて、ヒ素および銅を沈澱分離して得られた液のpHを
上げてカドミウムを水酸化物として沈澱分離することを
特徴とする製錬中間産物の処理方法。
4. The method for treating a smelting intermediate product according to claim 1, wherein the pH of a liquid obtained by precipitating and separating arsenic and copper is increased, and cadmium is precipitated and separated as hydroxide. Processing method of wrought intermediate products.
【請求項5】 前記製錬中間産物が銅製錬時に発生する
煙灰であることを特徴とする請求項1記載の製錬中間産
物の処理方法。
5. The method for treating a smelting intermediate product according to claim 1, wherein the smelting intermediate product is smoke ash generated during copper smelting.
【請求項6】 前記製錬中間産物が鉛製錬時に発生する
含銅ドロスであることを特徴とする請求項1記載の製錬
中間産物の処理方法。
6. The method for treating a smelting intermediate product according to claim 1, wherein the smelting intermediate product is a copper-containing dross generated during lead smelting.
JP4038151A 1992-02-25 1992-02-25 Treatment of smelting intermediates Expired - Lifetime JP3052535B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4038151A JP3052535B2 (en) 1992-02-25 1992-02-25 Treatment of smelting intermediates

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4038151A JP3052535B2 (en) 1992-02-25 1992-02-25 Treatment of smelting intermediates

Publications (2)

Publication Number Publication Date
JPH0625763A true JPH0625763A (en) 1994-02-01
JP3052535B2 JP3052535B2 (en) 2000-06-12

Family

ID=12517417

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4038151A Expired - Lifetime JP3052535B2 (en) 1992-02-25 1992-02-25 Treatment of smelting intermediates

Country Status (1)

Country Link
JP (1) JP3052535B2 (en)

Cited By (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100807929B1 (en) * 2005-09-29 2008-02-28 닛코 킨조쿠 가부시키가이샤 Copper converter dust treatment method
JP2008156687A (en) * 2006-12-22 2008-07-10 Sumitomo Metal Mining Co Ltd Method for separating impurity metal from refining dust
WO2009011075A1 (en) * 2007-07-13 2009-01-22 Dowa Metals & Mining Co., Ltd. Method of treating copper-arsenic compound
WO2009011316A1 (en) * 2007-07-13 2009-01-22 Dowa Metals & Mining Co., Ltd. Method of treating copper-arsenic compound
WO2009019799A1 (en) * 2007-08-09 2009-02-12 Dowa Metals & Mining Co., Ltd. Method of treating nonferrous smelting intermediate product containing arsenic
US8092764B2 (en) 2007-07-13 2012-01-10 Dowa Metals and Mining Co., Ltd. Method of processing non-ferrous smelting intermediate containing arsenic
US8092765B2 (en) 2007-08-09 2012-01-10 Dowa Metals and Mining Co., Ltd. Method of processing non-ferrous smelting intermediates containing arsenic
US8097228B2 (en) 2007-07-13 2012-01-17 Dowa Metals and Mining Co., Ltd. Method of processing diarsenic trioxide
CN102382980A (en) * 2011-11-02 2012-03-21 郴州丰越环保科技有限公司 Method for directly purifying cadmium from sponge cadmium
US8147779B2 (en) 2007-07-13 2012-04-03 Dowa Metals & Minning Co., Ltd. Method of alkali processing substance containing arsenic
JP2013237920A (en) * 2012-05-17 2013-11-28 Sumitomo Metal Mining Co Ltd Treatment method of copper smelting flue cinder
JP2018202383A (en) * 2017-05-30 2018-12-27 Jx金属株式会社 METHOD FOR REMOVING Sb METHOD FOR RECOVERING VALUABLE METAL
CN114182101A (en) * 2021-12-20 2022-03-15 昆明冶金研究院有限公司 Method for recycling copper in neutral leaching solution of zinc smelting
CN115572827A (en) * 2022-10-10 2023-01-06 江西理工大学 Method for selectively precipitating and recovering copper and arsenic from copper ash in steps
CN118460854A (en) * 2024-07-15 2024-08-09 山东恒邦冶炼股份有限公司 Method for cooperatively recovering valuable elements from high-arsenic alkaline wastewater and copper smelting electric dust

Cited By (17)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100807929B1 (en) * 2005-09-29 2008-02-28 닛코 킨조쿠 가부시키가이샤 Copper converter dust treatment method
JP2008156687A (en) * 2006-12-22 2008-07-10 Sumitomo Metal Mining Co Ltd Method for separating impurity metal from refining dust
US8110162B2 (en) 2007-07-13 2012-02-07 Dowa Metals & Mining Co., Ltd. Method of processing copper arsenic compound
WO2009011075A1 (en) * 2007-07-13 2009-01-22 Dowa Metals & Mining Co., Ltd. Method of treating copper-arsenic compound
WO2009011316A1 (en) * 2007-07-13 2009-01-22 Dowa Metals & Mining Co., Ltd. Method of treating copper-arsenic compound
US8092764B2 (en) 2007-07-13 2012-01-10 Dowa Metals and Mining Co., Ltd. Method of processing non-ferrous smelting intermediate containing arsenic
US8147779B2 (en) 2007-07-13 2012-04-03 Dowa Metals & Minning Co., Ltd. Method of alkali processing substance containing arsenic
US8097228B2 (en) 2007-07-13 2012-01-17 Dowa Metals and Mining Co., Ltd. Method of processing diarsenic trioxide
WO2009019799A1 (en) * 2007-08-09 2009-02-12 Dowa Metals & Mining Co., Ltd. Method of treating nonferrous smelting intermediate product containing arsenic
US8092765B2 (en) 2007-08-09 2012-01-10 Dowa Metals and Mining Co., Ltd. Method of processing non-ferrous smelting intermediates containing arsenic
CN102382980A (en) * 2011-11-02 2012-03-21 郴州丰越环保科技有限公司 Method for directly purifying cadmium from sponge cadmium
JP2013237920A (en) * 2012-05-17 2013-11-28 Sumitomo Metal Mining Co Ltd Treatment method of copper smelting flue cinder
JP2018202383A (en) * 2017-05-30 2018-12-27 Jx金属株式会社 METHOD FOR REMOVING Sb METHOD FOR RECOVERING VALUABLE METAL
CN114182101A (en) * 2021-12-20 2022-03-15 昆明冶金研究院有限公司 Method for recycling copper in neutral leaching solution of zinc smelting
CN115572827A (en) * 2022-10-10 2023-01-06 江西理工大学 Method for selectively precipitating and recovering copper and arsenic from copper ash in steps
CN115572827B (en) * 2022-10-10 2024-06-28 江西理工大学 Method for selectively precipitating and recovering copper and arsenic from copper ash step by step
CN118460854A (en) * 2024-07-15 2024-08-09 山东恒邦冶炼股份有限公司 Method for cooperatively recovering valuable elements from high-arsenic alkaline wastewater and copper smelting electric dust

Also Published As

Publication number Publication date
JP3052535B2 (en) 2000-06-12

Similar Documents

Publication Publication Date Title
US7615199B2 (en) Method for the recovery of valuable metals and arsenic from a solution
JP3756687B2 (en) Method for removing and fixing arsenic from arsenic-containing solutions
RU2023728C1 (en) Method of extracting zinc, copper, lead and silver from zinc-iron-containing sulfide stock
JP3052535B2 (en) Treatment of smelting intermediates
US4431613A (en) Leaching of sulphidic mattes containing non-ferrous metals and iron
EP1453985A1 (en) A method for precipitating iron from a zinc sulphate solution as hematite
FI74046B (en) TILLVARATAGANDE AV ZINK UR ZINK INNEHAOLLANDE SULFIDMATERIAL.
US4305914A (en) Process for precipitating iron as jarosite with a low non-ferrous metal content
JP3403289B2 (en) Method for separating arsenic contained in smelting intermediate and method for recovering arsenic
JPH085671B2 (en) Copper arsenate manufacturing method
CA1097507A (en) Process of treating residues from the leaching of roasted zinc blende
WO2001023628A1 (en) Stable ferric arsenate precipitation from acid copper solutions whilst minimising copper losses
JP3212875B2 (en) Arsenic recovery method
JP3197288B2 (en) Simultaneous wet treatment of zinc concentrate and zinc leaching residue
JP3411320B2 (en) Zinc smelting method
Dutrizac An overview of iron precipitation in hydrometallurgy
CA1238192A (en) Method for the recovery of germanium
WO1999018248A1 (en) Recovery of lead from flue dusts
JP2003137545A (en) Method for manufacturing waste acid gypsum
US5002748A (en) Method for the preparation of copper arsenate
KR101763549B1 (en) Method and arrangement of separating arsenic from starting materials
CN114269954A (en) Method for producing germanium concentrates from metallurgical residues
CN114341374A (en) Method for producing silver concentrates from metallurgical residues
JPH09137236A (en) Method for recovering cadmium and sponge cadmium.
CN113604676B (en) Method for processing residual pot powder

Legal Events

Date Code Title Description
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20000307

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080407

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090407

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090407

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100407

Year of fee payment: 10

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100407

Year of fee payment: 10

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100407

Year of fee payment: 10

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110407

Year of fee payment: 11

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120407

Year of fee payment: 12

EXPY Cancellation because of completion of term