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CN113832344B - Method for recovering copper and cobalt from copper-cobalt slag - Google Patents

Method for recovering copper and cobalt from copper-cobalt slag Download PDF

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CN113832344B
CN113832344B CN202010514161.8A CN202010514161A CN113832344B CN 113832344 B CN113832344 B CN 113832344B CN 202010514161 A CN202010514161 A CN 202010514161A CN 113832344 B CN113832344 B CN 113832344B
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copper
cobalt
slag
methanesulfonic acid
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CN113832344A (en
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何静
廖方文
代杰
曹姝琼
柳涛
陈永明
杨声海
唐朝波
杨建广
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    • 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
    • C22B7/006Wet processes
    • C22B7/007Wet processes by acid leaching
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/04Extraction of metal compounds from ores or concentrates by wet processes by leaching
    • C22B3/16Extraction of metal compounds from ores or concentrates by wet processes by leaching in organic solutions
    • C22B3/1608Leaching with acyclic or carbocyclic agents
    • C22B3/1616Leaching with acyclic or carbocyclic agents of a single type
    • C22B3/165Leaching with acyclic or carbocyclic agents of a single type with organic acids
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    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25CPROCESSES FOR THE ELECTROLYTIC PRODUCTION, RECOVERY OR REFINING OF METALS; APPARATUS THEREFOR
    • C25C1/00Electrolytic production, recovery or refining of metals by electrolysis of solutions
    • C25C1/12Electrolytic production, recovery or refining of metals by electrolysis of solutions of copper
    • 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
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    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

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Abstract

The invention belongs to the technical field of wet metallurgy, and particularly relates to a method for recovering copper and cobalt from copper-cobalt slag, which comprises the following steps: step (1): carrying out selective oxidation leaching on copper-cobalt slag and an oxidant in a methanesulfonic acid solution system, and then carrying out solid-liquid separation to obtain a copper-cobalt methanesulfonic acid leaching solution and metal impurity slag; step (2): and (4) performing electric replacement treatment on the copper-cobalt methanesulfonic acid leaching solution, and separating to obtain copper sponge and copper-cobalt removal solution. Compared with the traditional sulfuric acid system, the method selects methanesulfonic acid as the reaction system, can effectively realize the selective separation of each metal in the copper-cobalt slag, improves the recovery efficiency of copper and cobalt, and provides guidance for industrial production.

Description

一种从铜钴渣中回收铜、钴的方法A kind of method for recovering copper and cobalt from copper-cobalt slag

技术领域technical field

本发明涉及一种从铜钴渣中回收铜、钴的方法,属于湿法冶金技术领域。The invention relates to a method for recovering copper and cobalt from copper-cobalt slag, belonging to the technical field of hydrometallurgy.

背景技术Background technique

在湿法冶炼系统中会产出铜钴硫化物或氧化物的渣,渣中的铜钴具有很高的回收价值。因此实现对铜钴渣的高效资源化利用,具有显著的经济效益和社会效益。In the hydrometallurgical system, copper-cobalt sulfide or oxide slag will be produced, and the copper-cobalt in the slag has a high recovery value. Therefore, the efficient resource utilization of copper-cobalt slag has significant economic and social benefits.

为实现铜钴渣的有价元素的有效提取分离,我国许多专家学者也对铜钴渣的处置做了大量研究工作。例如,廖春发等采用铜钴选择性浸出-浸出液萃取铜并电积生产阴极铜-萃余液氧化中和除铁-除铁后液中和沉钴生产钴渣的工艺流程从铜钴氧化矿中回收分离铜钴,可以使铜浸出率大于95%,钴浸出率大于88%。唐朝波等采用火法还原熔炼的方法处理铜钴冶炼渣,在焦炭用量6%、黄铁矿用量20%、熔炼温度1350℃、保温时间3h的最佳工艺条件下,铜、钴回收率最高为92.95%和89.95%。In order to realize the effective extraction and separation of valuable elements of copper-cobalt slag, many experts and scholars in my country have also done a lot of research work on the disposal of copper-cobalt slag. For example, Liao Chunfa et al. adopted the selective leaching of copper and cobalt - leaching solution to extract copper and electrowinning to produce cathode copper - raffinate oxidation neutralization and iron removal - the process flow of liquid neutralization of cobalt precipitation to produce cobalt slag after iron removal from copper-cobalt oxide ore Recycling and separating copper and cobalt can make the copper leaching rate greater than 95% and the cobalt leaching rate greater than 88%. Tang Chaobo et al. used pyroreduction smelting to treat copper-cobalt smelting slag. Under the optimal process conditions of coke consumption of 6%, pyrite consumption of 20%, smelting temperature of 1350°C, and holding time of 3h, the highest recovery rate of copper and cobalt was 92.95% and 89.95%.

虽然,上述方法对渣料中的铜钴具有良好的回收效果,但回收效率仍不理想,此外,由于渣的特殊性,其含有大量性质和铜、钴类似的干扰杂质元素,这些杂质元素的存在严重干扰了铜、钴的提取选择性,很大程度导致所得产品品位下降。因此,行业内急需一种能够从杂质元素中高选择性提取铜、钴,并实现铜和钴高选择性分离的技术方案。Although the above method has a good recovery effect on copper and cobalt in the slag, the recovery efficiency is still unsatisfactory. In addition, due to the particularity of the slag, it contains a large number of interfering impurity elements similar to copper and cobalt. The existence of serious interference with the extraction selectivity of copper and cobalt, to a large extent, leads to a decrease in the grade of the obtained product. Therefore, there is an urgent need in the industry for a technical solution that can extract copper and cobalt from impurity elements with high selectivity and achieve high-selectivity separation of copper and cobalt.

发明内容SUMMARY OF THE INVENTION

本发明的目的是在于提供一种从铜钴渣中回收铜、钴的方法,旨在改善铜钴与杂质元素的分离选择性,并且改善铜与钴的分离选择性。The purpose of the present invention is to provide a method for recovering copper and cobalt from copper-cobalt slag, aiming at improving the separation selectivity of copper-cobalt and impurity elements, and improving the separation selectivity of copper and cobalt.

一种从铜钴渣中回收铜、钴的方法,包括以下步骤:A method for recovering copper and cobalt from copper-cobalt slag, comprising the following steps:

步骤(1):将铜钴渣、氧化剂在甲磺酸(本发明也称为甲基磺酸或CH3SO3H)溶液体系中进行选择性氧化浸出,随后固液分离,得到铜钴甲磺酸浸出液和金属杂质渣;所述的甲磺酸溶液中,甲磺酸的浓度为80~150g/L;Step (1): carry out selective oxidative leaching of copper-cobalt slag and oxidant in methanesulfonic acid (also referred to as methanesulfonic acid or CH 3 SO 3 H in the present invention) solution system, followed by solid-liquid separation to obtain copper-cobalt methyl methacrylate. Sulfonic acid leaching solution and metal impurity slag; in the methanesulfonic acid solution, the concentration of methanesulfonic acid is 80-150 g/L;

步骤(2):将铜钴甲磺酸浸出液进行电置换处理,分离得到海绵铜和脱铜钴液;其中,电置换过程中的电流密度为10~30mA/cm2Step (2): subject the copper-cobalt methanesulfonic acid leaching solution to electro-replacement treatment to separate the sponge copper and decopper-decobalt solution; wherein, the current density during the electro-replacement process is 10-30 mA/cm 2 .

铜钴渣中,除含有铜、钴外,还含有大量的杂质元素,这些杂质元素的性质大多和铜、钴的类似,将很大程度伴随铜、钴浸出,导致难于选择性分离;此外,铜钴渣的物相种类复杂,且各物相的浸出行为不一,这也会很大程度影响铜、钴的浸出回收。为解决铜钴渣中铜钴回收率不理想,以及铜钴与干扰杂质元素的分离选择性问题,本发明创新地发现,在甲磺酸体系下进行氧化浸出,配合所述的条件的控制,能够意外地改善铜钴与渣中的杂质元素的选择性问题,能够意外地实现铜钴的同步、高选择性、高回收率的浸出。不仅如此,在该创新地甲磺酸高选择性浸出的基础上,进一步配合在甲磺酸体系下的电置换反应以及电置换条件的联合控制,可以进一步协同改善铜和钴,以及铜和其他杂质元素的分离选择性,还可进一步改善铜的回收率,如此有助于在获得高质量铜的同时,还能获知高质量的钴。In addition to copper and cobalt, copper-cobalt slag also contains a large amount of impurity elements. The properties of these impurity elements are mostly similar to those of copper and cobalt, which will be accompanied by leaching of copper and cobalt to a large extent, resulting in difficulty in selective separation; in addition, The phase types of copper-cobalt slag are complex, and the leaching behavior of each phase is different, which will also greatly affect the leaching and recovery of copper and cobalt. In order to solve the problem of the unsatisfactory recovery rate of copper and cobalt in the copper-cobalt slag and the separation selectivity of copper and cobalt from interfering impurity elements, the present invention innovatively finds that oxidative leaching is carried out under the methanesulfonic acid system, and the control of the described conditions is carried out, The problem of selectivity between copper-cobalt and impurity elements in the slag can be unexpectedly improved, and the simultaneous, high-selectivity, and high-recovery leaching of copper-cobalt can be unexpectedly realized. Not only that, on the basis of the innovative high-selective leaching of methanesulfonic acid, the electro-displacement reaction under the methanesulfonic acid system and the combined control of electro-displacement conditions can further synergistically improve copper and cobalt, as well as copper and other The separation selectivity of impurity elements can further improve the recovery rate of copper, which helps to obtain high-quality cobalt while obtaining high-quality copper.

所述的铜钴渣为含有铜、钴以及金属杂质元素;所述的金属杂质元素为包含铁、铅、锑中的至少一种。The copper-cobalt slag contains copper, cobalt and metal impurity elements; the metal impurity element contains at least one of iron, lead and antimony.

优选地,其中的含铜10%~30%,含钴1%~10%,各金属杂质(单一金属杂质)的含量均不高于5%(也即是单个最大杂质不高于5%)。所述的含量指以渣干重计的金属的重量百分含量。Preferably, the copper content is 10% to 30%, and the cobalt content is 1% to 10%, and the content of each metal impurity (single metal impurity) is not higher than 5% (that is, the single largest impurity is not higher than 5%) . Said content refers to the weight percent content of metals based on the dry weight of the slag.

所述的铜钴渣在处理前,可以基于现有设备和手段进行干燥、破碎、球磨、筛分等处理。The copper-cobalt slag can be dried, crushed, ball milled, screened and other treatments based on existing equipment and means before being treated.

本发明技术方案,在所述的创新地甲磺酸体系下进行氧化浸出,能够出人意料地实现铜和钴的同步伴随浸出,不仅如此,还能够改善铜钴与杂质元素的分离选择性,能够有效改善铜钴的回收率,且降低杂质的伴随浸出率。研究还进一步发现,控制选择性氧化浸出过程的甲磺酸的浓度,有助于进一步改善铜钴与杂质的分离选择性。The technical solution of the present invention is to carry out oxidative leaching under the innovative methanesulfonic acid system, which can unexpectedly realize the simultaneous leaching of copper and cobalt, not only that, but also can improve the separation selectivity of copper, cobalt and impurity elements, and can effectively Improve the recovery rate of copper and cobalt, and reduce the accompanying leaching rate of impurities. The study further found that controlling the concentration of methanesulfonic acid in the selective oxidative leaching process can help to further improve the separation selectivity of copper and cobalt from impurities.

作为优选,所述的甲磺酸溶液中,甲磺酸的浓度为80~150g/L;优选为80~120g/L;Preferably, in the methanesulfonic acid solution, the concentration of methanesulfonic acid is 80-150 g/L; preferably 80-120 g/L;

铜钴渣与甲磺酸溶液的固液质量比为1:4~8。The solid-liquid mass ratio of the copper-cobalt slag to the methanesulfonic acid solution is 1:4-8.

作为优选,所述的氧化剂为双氧水。Preferably, the oxidant is hydrogen peroxide.

优选地,所述的氧化剂不低于将其中的铜、钴完全浸出的理论量;优选为理论量的1.2~1.5倍。Preferably, the oxidizing agent is not lower than the theoretical amount for completely leaching copper and cobalt therein; preferably, it is 1.2 to 1.5 times the theoretical amount.

作为优选,选择性氧化浸出过程的温度为30~90℃,优选为80~90℃。浸出时间优选为0.5~3h。Preferably, the temperature of the selective oxidative leaching process is 30-90°C, preferably 80-90°C. The leaching time is preferably 0.5 to 3 hours.

本发明还研究发现,创新地在甲磺酸体系下进行电置换,能够改善铜与钴的分离选择性,以及改善铜与其他杂质元素的分离选择性,有助于进一步改善获得的铜的质量,降低钴以及杂质元素的伴随置换,在该基础上,进一步协同配合甲磺酸体系下的选择性氧化浸出,能够协同改善铜与钴以及其他杂质元素的分离选择性。The invention also finds that the innovative electro-replacement under the methanesulfonic acid system can improve the separation selectivity of copper and cobalt, as well as the separation selectivity of copper and other impurity elements, which is helpful to further improve the quality of the obtained copper. , to reduce the concomitant replacement of cobalt and impurity elements. On this basis, the selective oxidative leaching under the methanesulfonic acid system is further coordinated, which can synergistically improve the separation selectivity of copper, cobalt and other impurity elements.

作为优选,采用铜钴甲磺酸浸出液为置换原液(本发明也称为电解液或者电沉积液);以金属板为阳极,惰性电极为阴极,浸入置换原液中,通电进行电置换。Preferably, the copper cobalt methanesulfonic acid leaching solution is used as the replacement stock solution (also referred to as electrolyte or electrodeposition solution in the present invention); the metal plate is used as the anode, and the inert electrode is used as the cathode, immersed in the replacement stock solution, and energized for electric replacement.

优选地,金属板为锌和/或铁。Preferably, the metal sheet is zinc and/or iron.

惰性阴极为石墨、钛网或不锈钢板。Inert cathodes are graphite, titanium mesh or stainless steel plates.

阴阳极板面积可以相同,也可不同,优选地,阴阳极板面积比优选为1:1。The area of the cathode and anode plates may be the same or different, and preferably, the area ratio of the cathode and anode plates is preferably 1:1.

极板间距为2~5cm。The distance between the plates is 2 to 5 cm.

本发明进一步研究发现,控制电置换过程的甲磺酸的浓度、电流密度以及温度,有助于进一步改善铜与钴以及其他杂质元素的分离选择性,有助于进一步改善电置换效果。Further research in the present invention finds that controlling the concentration, current density and temperature of methanesulfonic acid in the electro-displacement process helps to further improve the separation selectivity of copper, cobalt and other impurity elements, and helps to further improve the electro-displacement effect.

作为优选,步骤(2)中,控制铜钴甲磺酸浸出液中甲磺酸的浓度为20~80g/L,优选为30~70g/L。Preferably, in step (2), the concentration of methanesulfonic acid in the copper-cobalt methanesulfonic acid leaching solution is controlled to be 20-80 g/L, preferably 30-70 g/L.

优选地,调节电置换起始溶液的pH为0.2~3。Preferably, the pH of the electro-displacement starting solution is adjusted to be 0.2-3.

作为优选,电置换过程中的电流密度为10~30mA/cm2;进一步优选为10~20mA/cm2;更进一步优选为15~20mA/cm2Preferably, the current density during the electro-replacement process is 10-30 mA/cm 2 ; more preferably 10-20 mA/cm 2 ; still more preferably 15-20 mA/cm 2 .

作为优选,电置换过程的温度为30~80℃;进一步优选为50~70℃。Preferably, the temperature of the electric displacement process is 30-80°C; more preferably, it is 50-70°C.

本发明中,基于所述的甲磺酸选择性氧化浸出以及电置换,能够高回收率、高选择性地分离铜,且获得高质量的钴液,本发明中,可基于现有方法,对钴液进行处理,回收其中的钴。In the present invention, based on the selective oxidative leaching and electric displacement of methanesulfonic acid, copper can be separated with high recovery rate and high selectivity, and high-quality cobalt liquid can be obtained. The cobalt solution is processed to recover the cobalt contained therein.

作为优选,将获得的脱铜钴液与草酸发生沉淀反应,随后经煅烧处理,得到Co3O4Preferably, the obtained copper removal cobalt solution is subjected to a precipitation reaction with oxalic acid, and then calcined to obtain Co 3 O 4 .

作为优选,沉淀回收钴的过程中,用甲磺酸溶液调节反应终点pH值为1~3,草酸加入量为理论量的1.2~1.5倍,沉淀时间0.5~3h。Preferably, in the process of precipitating and recovering cobalt, methanesulfonic acid solution is used to adjust the pH value of the reaction end point to 1 to 3, the amount of oxalic acid added is 1.2 to 1.5 times the theoretical amount, and the precipitation time is 0.5 to 3 hours.

作为优选,沉淀反应中的温度为50~70℃。Preferably, the temperature in the precipitation reaction is 50 to 70°C.

本发明一种优选的从铜钴渣中回收铜、钴的方法,包括以下步骤:A preferred method for recovering copper and cobalt from copper-cobalt slag of the present invention comprises the following steps:

(1)铜钴渣为潮湿的结块体,经破碎、烘干、球磨、筛分后与甲磺酸溶液混合酸浸,浸出过程加入氧化剂,通过控制浸出工艺条件有效实现铜钴与杂质金属的分离,经真空抽滤得到含铜钴的甲磺酸盐溶液与含铁铅锑等金属杂质的浸出渣。(1) The copper-cobalt slag is a moist agglomerate. After crushing, drying, ball milling, and screening, it is mixed with methanesulfonic acid solution for acid leaching. The oxidant is added during the leaching process, and the copper-cobalt and impurity metals are effectively realized by controlling the leaching process conditions. The methanesulfonate solution containing copper and cobalt and the leaching slag containing metal impurities such as iron, lead and antimony are obtained by vacuum filtration.

(2)将步骤(1)所得含铜钴的甲磺酸盐溶液作为置换原液。根据金属间标准电极电势,以金属板为阳极,惰性电极为阴极,浸入置换原液中,控制置换参数通电后开始反应1-2h,得到高纯度海绵铜和含钴脱铜液。(2) The methanesulfonic acid salt solution containing copper and cobalt obtained in step (1) is used as the replacement stock solution. According to the standard electrode potential between metals, take the metal plate as the anode and the inert electrode as the cathode, immerse in the replacement stock solution, control the replacement parameters and start the reaction for 1-2 hours after electrification, to obtain high-purity sponge copper and cobalt-containing copper removal solution.

(3)将步骤(2)所得含钴脱铜液加热至50~70℃,在搅拌过程中缓慢加入草酸,得到草酸钴沉淀,草酸钴经过高温煅烧得到Co3O4(3) heating the cobalt-containing copper removal solution obtained in step (2) to 50-70° C., slowly adding oxalic acid in the stirring process to obtain cobalt oxalate precipitation, and calcining cobalt oxalate at high temperature to obtain Co 3 O 4 .

本发明的有益效果:Beneficial effects of the present invention:

1、本发明创新地发现,在甲磺酸有机酸体系下进行氧化浸出,能够意外地改善铜钴渣中铜钴与铁铅锑等杂质金属的分离选择性,能够实现铜、钴的同步、高选择性浸出,且降低铁铅锑等杂质金属的伴随浸出率。研究发现,相比于传统硫酸体系,更有效实现金属间的选择性分离;整个过程采用甲磺酸有机体系,过程绿色环保,且对设备腐蚀性较小,同时金属回收效率更高。1. The present invention innovatively finds that oxidative leaching under the methanesulfonic acid organic acid system can unexpectedly improve the separation selectivity of copper-cobalt and iron-lead-antimony and other impurity metals in the copper-cobalt slag, and can realize the synchronization of copper and cobalt, High selective leaching, and reduce the accompanying leaching rate of impurity metals such as iron, lead and antimony. The study found that compared with the traditional sulfuric acid system, the selective separation of metals is more effectively achieved; the whole process adopts methanesulfonic acid organic system, which is green and environmentally friendly, and is less corrosive to equipment, and at the same time, the metal recovery efficiency is higher.

2、创新地在甲磺酸体系下进行电置换,得益于所述的甲磺酸体系,有助于改善铜和钴的电置换分离选择性。本发明所述的加强电置换提铜,减少了传统置换过程中原料的消耗,置换过程控制反应各项工艺参数,所得海绵铜纯度达98%以上,电流效率和金属回收率都大幅度提高。2. The electro-displacement is innovatively carried out under the methanesulfonic acid system, which helps to improve the electro-displacement separation selectivity of copper and cobalt thanks to the methanesulfonic acid system. The enhanced electric displacement copper extraction of the invention reduces the consumption of raw materials in the traditional displacement process, and the displacement process controls various process parameters of the reaction, the obtained sponge copper has a purity of more than 98%, and the current efficiency and metal recovery rate are greatly improved.

3、在所述的创新的甲磺酸体系进行电置换,进一步对体系的甲磺酸体系、电流密度以及温度的联合控制,能够进一步改善铜与其他金属的分离选择性。3. Electro-replacement is carried out in the innovative methanesulfonic acid system, and the combined control of the methanesulfonic acid system, current density and temperature of the system can further improve the separation selectivity of copper and other metals.

4、基于所述的创新的甲磺酸选择性氧化浸出以及甲磺酸电置换的联合,可以进一步协同,改善铜和钴的分离选择性,有助于改善回收铜和钴的品位。4. Based on the innovative combination of methanesulfonic acid selective oxidative leaching and methanesulfonic acid electro-displacement, it can further synergize, improve the separation selectivity of copper and cobalt, and help to improve the quality of copper and cobalt recovered.

5、研究发现,在所述的铜钴渣中,可以高选择性地获得铜产品和钴产品,且各自的产品的品位可达到98%以上,且回收率均可达到93%以上。5. The study found that in the copper-cobalt slag, copper products and cobalt products can be obtained with high selectivity, and the grades of the respective products can reach more than 98%, and the recovery rate can reach more than 93%.

6、本发明整个工艺操作简单,能耗较低,所得产品质量高,使铜钴渣中的铜钴得到了有效分离和高效回收。此外,处理过程不会存在设备腐蚀问题,绿色高效,有利于实现资源的综合利用。6. The whole process of the present invention has the advantages of simple operation, low energy consumption, and high quality of the obtained product, so that the copper and cobalt in the copper-cobalt slag can be effectively separated and efficiently recovered. In addition, there is no equipment corrosion problem in the treatment process, which is green and efficient, and is conducive to the comprehensive utilization of resources.

附图说明Description of drawings

附图1为本发明在甲磺酸体系下从铜钴渣中回收铜钴的流程图。Accompanying drawing 1 is the flow chart that the present invention recovers copper-cobalt from copper-cobalt slag under methanesulfonic acid system.

附图2中(1)(2)为海绵铜SEM图。(1) and (2) in Fig. 2 are SEM images of sponge copper.

具体实施方式Detailed ways

以下结合例子对本发明做进一步的说明。The present invention will be further described below in conjunction with examples.

以下案例,所述的渣中的金属含量指,以渣干重计,各金属的重量百分含量。In the following cases, the metal content in the slag refers to the weight percent content of each metal based on the dry weight of the slag.

实施例1:Example 1:

(1)将铜钴渣(含铜15.24%、钴3.17%、铁1.01%、铅2.14%、锑0.84%)破碎、烘干、球磨、筛分至-200~-170目后称取100g按液固比5:1与80g/L甲磺酸溶液混合酸浸,以1mL/min的流速加入H2O2,搅拌速度为300r/min,在温度为60℃下反应浸出1h后经真空抽滤得到含铜钴的甲磺酸盐溶液,此时铜钴的浸出率分别为96.31%、94.52%,而铁、铅、锑的浸出率为1.20%、1.38%、0.74%,铜钴与铁铅锑等杂质分离效果好,相较于现有无机酸浸或氨浸,铜钴浸出率以及浸出选择性都有所提高。(1) Crushing, drying, ball milling, sieving to -200~-170 mesh, weighing 100g Liquid-solid ratio of 5:1 was mixed with 80g/L methanesulfonic acid solution for acid leaching, H 2 O 2 was added at a flow rate of 1 mL/min, and the stirring speed was 300 r/min. The methanesulfonate solution containing copper and cobalt was obtained by filtration. At this time, the leaching rates of copper and cobalt were 96.31% and 94.52% respectively, while the leaching rates of iron, lead and antimony were 1.20%, 1.38% and 0.74%. The separation effect of impurities such as lead and antimony is good. Compared with the existing inorganic acid leaching or ammonia leaching, the leaching rate and leaching selectivity of copper and cobalt are improved.

(2)以步骤(1)所得含铜钴的甲磺酸盐溶液为置换原液(调节pH=1.0),取该液400mL置于500mL反应槽中,其中甲磺酸浓度为50g/L。使用导线将金属锌板(尺寸2mm×70mm×120mm)接入直流稳压电源正极,钛网(尺寸70mm×120mm,网孔2×7mm)接入电源负极,将两极板浸入溶液,通电作用下进行实验操作,每隔一段时间刮去阴阳极沉积物。两极板间距为3cm,电流密度为10mA/cm2,反应槽置于恒温水浴槽中,控制反应温度为50℃,反应时间为2h,铜的置换率达到93.14%,海绵铜纯度为98.35%,海绵铜中铁、铅、锑、钴含量分别为0.26%、0.37%、0.12%、0.09%。钛网使用后以废酸浸泡,锌板可反复使用直至溶穿。(2) Taking the methanesulfonic acid salt solution containing copper and cobalt obtained in step (1) as the replacement stock solution (adjusting pH=1.0), taking 400 mL of this solution and placing it in a 500 mL reaction tank, wherein the methanesulfonic acid concentration is 50 g/L. Use a wire to connect the metal zinc plate (size 2mm×70mm×120mm) to the positive electrode of the DC stabilized power supply, and the titanium mesh (size 70mm×120mm, mesh 2×7mm) to connect to the negative electrode of the power supply, and immerse the two-pole plate in the solution. Carry out the experimental operation, scraping off the cathodic and anodic deposits at regular intervals. The distance between the two polar plates is 3cm, the current density is 10mA/cm 2 , the reaction tank is placed in a constant temperature water bath, the reaction temperature is controlled to 50°C, the reaction time is 2h, the copper replacement rate is 93.14%, and the purity of the sponge copper is 98.35%. The content of iron, lead, antimony and cobalt in the sponge copper is 0.26%, 0.37%, 0.12% and 0.09% respectively. The titanium mesh is soaked in waste acid after use, and the zinc plate can be used repeatedly until it dissolves.

(3)将步骤(2)所得脱铜液加热至50℃,在200r/min搅拌过程中缓慢加入5.63g草酸,经过2h沉淀,用甲磺酸溶液调节反应终点pH值为2.0,得到含钴草酸钴沉淀8.93g,钴的总回收率达93.64%。(3) heating the decopper solution obtained in step (2) to 50°C, slowly adding 5.63 g of oxalic acid in the process of stirring at 200 r/min, after 2 h of precipitation, adjusting the pH value of the reaction end point to 2.0 with methanesulfonic acid solution to obtain cobalt-containing 8.93 g of cobalt oxalate was precipitated, and the total recovery rate of cobalt was 93.64%.

对比例1:Comparative Example 1:

和实施例1相比,区别仅在于,将处理工艺中所采用的甲磺酸替换成硫酸,且酸的浓度等其他操作均相同。Compared with Example 1, the only difference is that the methanesulfonic acid used in the treatment process is replaced with sulfuric acid, and other operations such as the acid concentration are the same.

结果为:The result is:

步骤(1)中,此时铜钴的浸出率分别为93.83%、91.43%,铁、铅、锑的浸出率为7.20%、8.19%、5.47%。电置换过程铜的置换率为91.32%,海绵铜纯度为92.14%,海绵铜中铁、铅、锑、钴含量分别为0.92%、1.81%、0.67%、0.13%。与实施例1相比铜钴浸出率降低,而铁铅锑等金属杂质浸出率上升,回收金属与杂质金属没有得到有效分离,导致后续海绵铜品位的下降。In step (1), the leaching rates of copper and cobalt are 93.83% and 91.43%, respectively, and the leaching rates of iron, lead and antimony are 7.20%, 8.19% and 5.47%. The replacement rate of copper in the electrical replacement process was 91.32%, and the purity of the sponge copper was 92.14%. Compared with Example 1, the leaching rate of copper and cobalt decreased, while the leaching rate of metal impurities such as iron, lead, and antimony increased, and the recovered metal and the impurity metal were not effectively separated, resulting in a subsequent drop in the grade of sponge copper.

实施例2:Example 2:

(1)将铜钴渣(含铜15.24%、钴3.17%、铁1.01%、铅2.14%、锑0.84%)破碎、烘干、球磨、筛分至-200~-170目后称取100g按液固比5:1与90g/L甲磺酸溶液混合酸浸,以1mL/min的流速加入H2O2,搅拌速度为300r/min,在温度为70℃下反应浸出1h后经真空抽滤得到含铜钴的甲磺酸盐溶液,此时铜钴的浸出率分别为97.58%、94.72%,铁、铅、锑的浸出率为1.06%、1.43%、0.65%,铜钴与铁铅锑等杂质分离效果好。(1) Crushing, drying, ball milling, sieving to -200~-170 mesh, weighing 100g Liquid-solid ratio of 5:1 was mixed with 90g/L methanesulfonic acid solution for acid leaching, H 2 O 2 was added at a flow rate of 1 mL/min, and the stirring speed was 300 r/min. The methanesulfonate solution containing copper and cobalt was obtained by filtration. At this time, the leaching rates of copper and cobalt were 97.58% and 94.72% respectively, and the leaching rates of iron, lead and antimony were 1.06%, 1.43% and 0.65%. The separation effect of impurities such as antimony is good.

(2)以步骤(1)所得含铜钴的甲磺酸盐溶液为置换原液(调节pH=1.0),取该液400mL置于500mL反应槽中,其中甲磺酸浓度为30g/L使用导线将金属锌板(尺寸2mm×70mm×120mm)接入直流稳压电源正极,钛网(尺寸70mm×120mm,网孔2×7mm)接入电源负极,将两极板浸入溶液,通电作用下进行实验操作,每隔一段时间刮去阴阳极沉积物。两极板间距为3cm,电流密度为15mA/cm2,反应槽置于恒温水浴槽中,控制反应温度为60℃,反应时间为2h,铜的置换率达到94.26%,海绵铜纯度为99.10%,海绵铜中铁、铅、锑、钴含量分别为0.20%、0.28%、0.15%、0.07%)。钛网使用后以废酸浸泡,锌板可反复使用直至溶穿。(2) Taking the methanesulfonic acid salt solution containing copper and cobalt obtained in step (1) as the replacement stock solution (adjusting pH=1.0), taking 400 mL of this solution and placing it in a 500 mL reaction tank, wherein the methanesulfonic acid concentration is 30 g/L using a wire Connect the metal zinc plate (size 2mm×70mm×120mm) to the positive electrode of the DC stabilized power supply, connect the titanium mesh (size 70mm×120mm, mesh 2×7mm) to the negative electrode of the power supply, immerse the two-pole plate in the solution, and conduct the experiment under the action of electricity operation, scraping off cathodic and anodic deposits at regular intervals. The distance between the two polar plates is 3cm, the current density is 15mA/cm 2 , the reaction tank is placed in a constant temperature water bath, the reaction temperature is controlled to be 60°C, the reaction time is 2h, the copper replacement rate is 94.26%, and the purity of the sponge copper is 99.10%. The content of iron, lead, antimony and cobalt in the sponge copper are 0.20%, 0.28%, 0.15% and 0.07% respectively). The titanium mesh is soaked in waste acid after use, and the zinc plate can be used repeatedly until it dissolves.

(3)将步骤(2)所得脱铜液加热至70℃,在200r/min搅拌过程中缓慢加入5.78g草酸,经过1.5h沉淀,用甲磺酸溶液调节反应终点pH值为2.0,得到草酸钴沉淀9.01g,钴的总回收率达93.86%。(3) heating the decopper solution obtained in step (2) to 70°C, slowly adding 5.78g oxalic acid in the process of stirring at 200r/min, after 1.5h precipitation, adjusting the pH value of the reaction end point to 2.0 with methanesulfonic acid solution to obtain oxalic acid 9.01 g of cobalt was precipitated, and the total recovery rate of cobalt was 93.86%.

实施例3:Example 3:

(1)将铜钴渣(含铜15.24%、钴3.17%、铁1.01%、铅2.14%、锑0.84%)破碎、烘干、球磨、筛分至-200~-170目后称取100g按液固比5:1与80g/L甲磺酸溶液混合酸浸,以1mL/min的流速加入H2O2,搅拌速度为300r/min,在温度为70℃下反应浸出1h后经真空抽滤得到含铜钴的甲磺酸盐溶液,此时铜钴的浸出率分别为96.45%、93.61%,铁、铅、锑的浸出率为0.81%、0.75%、0.63%,铜钴与铁铅锑等杂质分离效果好。(1) Crushing, drying, ball milling, sieving to -200~-170 mesh, weighing 100g Liquid-solid ratio of 5:1 was mixed with 80 g/L methanesulfonic acid solution for acid leaching, H 2 O 2 was added at a flow rate of 1 mL/min, and the stirring speed was 300 r/min. The methanesulfonate solution containing copper and cobalt was obtained by filtration. At this time, the leaching rates of copper and cobalt were 96.45% and 93.61% respectively, and the leaching rates of iron, lead and antimony were 0.81%, 0.75% and 0.63%. The separation effect of impurities such as antimony is good.

(2)以步骤(1)所得含铜钴的甲磺酸盐溶液为置换原液(调节pH=2.0),取该液400mL置于500mL反应槽中,其中甲磺酸浓度为40g/L。使用导线将金属锌板(尺寸2mm×70mm×120mm)接入直流稳压电源正极,钛网(尺寸70mm×120mm,网孔2×7mm)接入电源负极,将两极板浸入溶液,通电作用下进行实验操作,每隔一段时间刮去阴阳极沉积物。两极板间距为3cm,电流密度为15mA/cm2,反应槽置于恒温水浴槽中,控制反应温度为60℃,反应时间为2h,铜的置换率达到94.48%,海绵铜纯度为98.72%,海绵铜中铁、铅、锑、钴含量分别为0.23%、0.35%、0.14%、0.11%)。钛网使用后以废酸浸泡,锌板可反复使用直至溶穿。(2) Taking the methanesulfonic acid salt solution containing copper and cobalt obtained in step (1) as the replacement stock solution (adjusting pH=2.0), taking 400 mL of this solution and placing it in a 500 mL reaction tank, wherein the methanesulfonic acid concentration is 40 g/L. Use a wire to connect the metal zinc plate (size 2mm×70mm×120mm) to the positive electrode of the DC stabilized power supply, and the titanium mesh (size 70mm×120mm, mesh 2×7mm) to connect to the negative electrode of the power supply, and immerse the two-pole plate in the solution. Carry out the experimental operation, scraping off the cathodic and anodic deposits at regular intervals. The distance between the two polar plates is 3cm, the current density is 15mA/cm 2 , the reaction tank is placed in a constant temperature water bath, the reaction temperature is controlled to 60°C, the reaction time is 2h, the copper replacement rate is 94.48%, and the purity of the sponge copper is 98.72%. The content of iron, lead, antimony and cobalt in sponge copper are 0.23%, 0.35%, 0.14% and 0.11% respectively). The titanium mesh is soaked in waste acid after use, and the zinc plate can be used repeatedly until it dissolves.

(3)将步骤(2)所得脱铜液加热至70℃,在200r/min搅拌过程中缓慢加入5.83g草酸,经过1.5h沉淀,用甲磺酸溶液调节反应终点pH值为2.0,得到草酸钴沉淀9.12g,钴的总回收率达93.79%。(3) heating the decopper solution obtained in step (2) to 70°C, slowly adding 5.83 g of oxalic acid during stirring at 200 r/min, and precipitating for 1.5 h, adjusting the pH value of the reaction end point to 2.0 with methanesulfonic acid solution to obtain oxalic acid 9.12 g of cobalt was precipitated, and the total recovery rate of cobalt was 93.79%.

实施例4:Example 4:

(1)将与实施例1-3含量不同的铜钴渣(含铜18.14%、钴5.38%、铁1.23%、铅3.17%、锑0.69%)破碎、烘干、球磨、筛分至-200~-170目后称取100g按液固比5:1与80g/L甲磺酸溶液混合酸浸,以1mL/min的流速加入H2O2,搅拌速度为300r/min,在温度为70℃下反应浸出1h后经真空抽滤得到含铜钴的甲磺酸盐溶液,此时铜钴的浸出率分别为96.72%、94.08%,铁、铅、锑的浸出率为0.72%、0.77%、0.56%,铜钴与铁铅锑等杂质分离效果好。(1) The copper-cobalt slag (containing 18.14% copper, 5.38% cobalt, 1.23% iron, 3.17% lead, and 0.69% antimony) with a different content from Example 1-3 is crushed, dried, ball milled, and sieved to -200 After ~-170 mesh, weigh 100 g of mixed acid leaching with 80 g/L methanesulfonic acid solution at a liquid-solid ratio of 5:1, add H 2 O 2 at a flow rate of 1 mL/min, stir at a speed of 300 r/min, and at a temperature of 70 After reaction leaching at ℃ for 1 h, the methanesulfonate solution containing copper and cobalt was obtained by vacuum filtration. At this time, the leaching rates of copper and cobalt were 96.72% and 94.08%, respectively, and the leaching rates of iron, lead and antimony were 0.72% and 0.77%. , 0.56%, and the separation effect of impurities such as copper, cobalt and iron, lead and antimony is good.

(2)以步骤(1)所得含铜钴的甲磺酸盐溶液为置换原液(调节pH=2.0),取该液400mL置于500mL反应槽中,其中甲磺酸浓度为40g/L。使用导线将金属锌板(尺寸2mm×70mm×120mm)接入直流稳压电源正极,钛网(尺寸70mm×120mm,网孔2×7mm)接入电源负极,将两极板浸入溶液,通电作用下进行实验操作,每隔一段时间刮去阴阳极沉积物。两极板间距为3cm,电流密度为15mA/cm2,反应槽置于恒温水浴槽中,控制反应温度为60℃,反应时间为2h,铜的置换率达到95.24%,海绵铜纯度为98.71%,海绵铜中铁、铅、锑、钴含量分别为0.24%、0.33%、0.10%、0.12%。钛网使用后以废酸浸泡,锌板可反复使用直至溶穿。(2) Taking the methanesulfonic acid salt solution containing copper and cobalt obtained in step (1) as the replacement stock solution (adjusting pH=2.0), taking 400 mL of this solution and placing it in a 500 mL reaction tank, wherein the methanesulfonic acid concentration is 40 g/L. Use a wire to connect the metal zinc plate (size 2mm×70mm×120mm) to the positive electrode of the DC stabilized power supply, and the titanium mesh (size 70mm×120mm, mesh 2×7mm) to connect to the negative electrode of the power supply, and immerse the two-pole plate in the solution. Carry out the experimental operation, scraping off the cathodic and anodic deposits at regular intervals. The distance between the two polar plates is 3cm, the current density is 15mA/cm 2 , the reaction tank is placed in a constant temperature water bath, the reaction temperature is controlled to 60°C, the reaction time is 2h, the copper replacement rate is 95.24%, and the purity of the sponge copper is 98.71%. The content of iron, lead, antimony and cobalt in the sponge copper is 0.24%, 0.33%, 0.10% and 0.12% respectively. The titanium mesh is soaked in waste acid after use, and the zinc plate can be used repeatedly until it dissolves.

(3)将步骤(2)所得脱铜液加热至70℃,在200r/min搅拌过程中缓慢加入7.43g草酸,经过1.5h沉淀,用甲磺酸溶液调节反应终点pH值为2.0,得到草酸钴沉淀12.16g,钴的总回收率达93.82%。(3) heating the decopper solution obtained in step (2) to 70°C, slowly adding 7.43g of oxalic acid in the process of stirring at 200r/min, after 1.5h of precipitation, adjusting the pH value of the reaction end point to 2.0 with methanesulfonic acid solution to obtain oxalic acid 12.16g of cobalt was precipitated, and the total recovery rate of cobalt was 93.82%.

实施例5:Example 5:

调整选择性浸出条件,具体为:Adjust the selective leaching conditions, specifically:

(1)将铜钴渣(含铜15.24%、钴3.17%、铁1.01%、铅2.14%、锑0.84%)破碎、烘干、球磨、筛分至-200~-170目后称取100g按液固比5:1与120g/L甲磺酸溶液混合酸浸,以1mL/min的流速加入H2O2,搅拌速度为300r/min,在温度为80℃下反应浸出1h后经真空抽滤得到含铜钴的甲磺酸盐溶液,此时铜钴的浸出率分别为98.68%、96.37%,铁、铅、锑的浸出率为1.03%、1.28%、0.47%,铜钴与铁铅锑等杂质分离效果好。(1) Crushing, drying, ball milling, sieving to -200~-170 mesh, weighing 100g The liquid-solid ratio of 5:1 was mixed with 120g/L methanesulfonic acid solution for acid leaching, H 2 O 2 was added at a flow rate of 1 mL/min, the stirring speed was 300 r/min, and the reaction was leached at a temperature of 80 ° C for 1 hour, and then vacuumed. The methanesulfonate solution containing copper and cobalt was obtained by filtration. At this time, the leaching rates of copper and cobalt were 98.68% and 96.37% respectively, and the leaching rates of iron, lead and antimony were 1.03%, 1.28% and 0.47%. The separation effect of impurities such as antimony is good.

(2)以步骤(1)所得含铜钴的甲磺酸盐溶液为置换原液(调节pH=1.0),取该液400mL置于500mL反应槽中,其中甲磺酸浓度为40g/L。使用导线将金属锌板(尺寸2mm×70mm×120mm)接入直流稳压电源正极,钛网(尺寸70mm×120mm,网孔2×7mm)接入电源负极,将两极板浸入溶液,通电作用下进行实验操作,每隔一段时间刮去阴阳极沉积物。两极板间距为3cm,电流密度为15mA/cm2,反应槽置于恒温水浴槽中,控制反应温度为60℃,反应时间为2h,铜的置换率达到94.52%,海绵铜纯度为98.81%,海绵铜中铁、铅、锑、钴含量分别为0.21%、0.32%、0.11%、0.09%。钛网使用后以废酸浸泡,锌板可反复使用直至溶穿。(2) Taking the methanesulfonic acid salt solution containing copper and cobalt obtained in step (1) as the replacement stock solution (adjusting pH=1.0), taking 400 mL of this solution and placing it in a 500 mL reaction tank, wherein the methanesulfonic acid concentration is 40 g/L. Use a wire to connect the metal zinc plate (size 2mm×70mm×120mm) to the positive electrode of the DC stabilized power supply, and connect the titanium mesh (size 70mm×120mm, mesh 2×7mm) to the negative electrode of the power supply, and immerse the two-pole plate in the solution. Carry out the experimental operation, scraping off the cathodic and anodic deposits at regular intervals. The distance between the two polar plates is 3cm, the current density is 15mA/cm 2 , the reaction tank is placed in a constant temperature water bath, the reaction temperature is controlled to be 60°C, the reaction time is 2h, the copper replacement rate is 94.52%, and the purity of the sponge copper is 98.81%. The content of iron, lead, antimony and cobalt in sponge copper is 0.21%, 0.32%, 0.11% and 0.09% respectively. The titanium mesh is soaked in waste acid after use, and the zinc plate can be used repeatedly until it dissolves.

(3)将步骤(2)所得脱铜液加热至70℃,在200r/min搅拌过程中缓慢加入5.75g草酸,经过1.5h沉淀,用甲磺酸溶液调节反应终点pH值为2.0,得到草酸钴沉淀9.10g,钴的总回收率达94.01%。(3) heating the decopper solution obtained in step (2) to 70°C, slowly adding 5.75g oxalic acid during stirring at 200 r/min, and precipitating for 1.5 hours, adjusting the pH value of the reaction end point to 2.0 with methanesulfonic acid solution to obtain oxalic acid 9.10 g of cobalt was precipitated, and the total recovery rate of cobalt was 94.01%.

实施例6:Example 6:

和实施例5相比,区别主要在于,调整选择性电置换条件,具体为:Compared with Example 5, the main difference is that the selective electrical displacement conditions are adjusted, specifically:

(1)同实施例5步骤(1)。(1) step (1) with embodiment 5.

(2)以步骤(1)所得含铜钴的甲磺酸盐溶液为置换原液,取该液400mL置于500mL反应槽中,其中甲磺酸浓度为60g/L。使用导线将金属锌板(尺寸2mm×70mm×120mm)接入直流稳压电源正极,钛网(尺寸70mm×120mm,网孔2×7mm)接入电源负极,将两极板浸入溶液,通电作用下进行实验操作,每隔一段时间刮去阴阳极沉积物。两极板间距为3cm,电流密度为15mA/cm2,反应槽置于恒温水浴槽中,控制反应温度为70℃,反应时间为2h,铜的置换率达到95.87%,海绵铜纯度为98.86%,海绵铜中铁、铅、锑、钴含量分别为0.19%、0.24%、0.08%、0.07%。钛网使用后以废酸浸泡,锌板可反复使用直至溶穿。(2) Taking the methanesulfonic acid salt solution containing copper and cobalt obtained in step (1) as the replacement stock solution, 400 mL of this solution was taken and placed in a 500 mL reaction tank, wherein the methanesulfonic acid concentration was 60 g/L. Use a wire to connect the metal zinc plate (size 2mm×70mm×120mm) to the positive electrode of the DC stabilized power supply, and the titanium mesh (size 70mm×120mm, mesh 2×7mm) to connect to the negative electrode of the power supply, and immerse the two-pole plate in the solution. Carry out the experimental operation, scraping off the cathodic and anodic deposits at regular intervals. The distance between the two polar plates is 3cm, the current density is 15mA/cm 2 , the reaction tank is placed in a constant temperature water bath, the reaction temperature is controlled to be 70°C, the reaction time is 2h, the copper replacement rate is 95.87%, and the purity of the sponge copper is 98.86%. The content of iron, lead, antimony and cobalt in sponge copper is 0.19%, 0.24%, 0.08% and 0.07% respectively. The titanium mesh is soaked in waste acid after use, and the zinc plate can be used repeatedly until it dissolves.

(3)将步骤(2)所得脱铜液加热至70℃,在200r/min搅拌过程中缓慢加入5.73g草酸,经过1.5h沉淀,用甲磺酸溶液调节反应终点pH值为2.0,得到草酸钴沉淀9.17g,钴的总回收率达93.97%。(3) heating the copper removal solution obtained in step (2) to 70°C, slowly adding 5.73 g of oxalic acid in the process of stirring at 200 r/min, after 1.5 h of precipitation, adjusting the pH value of the reaction end point with methanesulfonic acid solution to 2.0 to obtain oxalic acid 9.17g of cobalt was precipitated, and the total recovery rate of cobalt was 93.97%.

对比例2Comparative Example 2

和实施例6相比,区别仅在于,将步骤(2)所采用的甲磺酸替换成硫酸,且酸的浓度等其他操作均相同。Compared with Example 6, the difference is only that the methanesulfonic acid used in step (2) is replaced with sulfuric acid, and other operations such as the acid concentration are the same.

结果为:The result is:

电置换过程铜的置换率为91.71%,海绵铜纯度为92.51%,海绵铜中铁、铅、锑、钴含量分别为0.47%、0.78%、0.56%、0.16%。与实施例6相比海绵铜的置换率与纯度下降,杂质离子含量增加。The replacement rate of copper in the electrical replacement process was 91.71%, and the purity of the sponge copper was 92.51%. Compared with Example 6, the replacement rate and purity of sponge copper decreased, and the content of impurity ions increased.

对比例3Comparative Example 3

和实施例6相比,区别仅在于,步骤(1)浸出采用甲磺酸浓度为50g/L,其他操作均相同。Compared with Example 6, the only difference is that the concentration of methanesulfonic acid used in the leaching in step (1) is 50 g/L, and other operations are the same.

结果为:The result is:

步骤(1)中,此时铜钴的浸出率分别为90.05%、89.63%,铁、铅、锑的浸出率为7.52%、8.93%、6.14%。电置换过程铜的置换率为93.68%,海绵铜纯度为94.14%,海绵铜中铁、铅、锑、钴含量分别为0.26%、0.72%、0.34%、0.14%。与实施例6相比铜钴浸出率降低,而铁铅锑等金属杂质浸出率上升,回收金属与杂质金属没有得到有效分离,导致后续海绵铜中杂质金属的含量相对上升,海绵铜品位从98.86%下降至94.14%。说明浸出过程甲磺酸浓度过低会影响金属的选择性浸出。In step (1), the leaching rates of copper and cobalt are 90.05% and 89.63%, respectively, and the leaching rates of iron, lead and antimony are 7.52%, 8.93% and 6.14%. The replacement rate of copper in the electrical replacement process was 93.68%, the purity of the sponge copper was 94.14%, and the iron, lead, antimony, and cobalt contents in the sponge copper were 0.26%, 0.72%, 0.34%, and 0.14%, respectively. Compared with Example 6, the leaching rate of copper and cobalt decreased, and the leaching rate of metal impurities such as iron, lead, and antimony increased, and the recovered metal and the impurity metal were not effectively separated, resulting in a relative increase in the content of the impurity metal in the subsequent sponge copper, and the grade of the sponge copper increased from 98.86 % fell to 94.14%. It shows that the low concentration of methanesulfonic acid in the leaching process will affect the selective leaching of metals.

对比例4Comparative Example 4

和实施例6相比,区别仅在于,步骤(2)置换过程设置电流密度为40mA/cm2,其他操作均相同。Compared with Example 6, the only difference is that the replacement process in step (2) sets the current density to 40 mA/cm 2 , and other operations are the same.

结果为:The result is:

电置换过程铜的置换率为90.16%,海绵铜纯度为91.14%,海绵铜中铁、铅、锑、钴含量分别为0.73%、0.81%、0.64%、0.24%。与实施例5相比海绵铜的置换率与纯度下降,杂质离子含量明显增加,说明电流密度过大会将杂质金属置换出来,与铜的置换形成竞争。The replacement rate of copper in the electrical replacement process was 90.16%, and the purity of the sponge copper was 91.14%. Compared with Example 5, the replacement rate and purity of sponge copper decreased, and the content of impurity ions increased significantly, indicating that the current density was too high to replace the impurity metal, which competed with the replacement of copper.

Claims (16)

1.一种从铜钴渣中回收铜、钴的方法,其特征在于,包括以下步骤:1. a method for recovering copper, cobalt from copper-cobalt slag, is characterized in that, comprises the following steps: 步骤(1):将铜钴渣、氧化剂在甲磺酸溶液体系中进行选择性氧化浸出,随后固液分离,得到铜钴甲磺酸浸出液和金属杂质渣;所述的甲磺酸溶液中,甲磺酸的浓度为80~150g/L;Step (1): carry out selective oxidation leaching of copper cobalt slag and oxidant in a methanesulfonic acid solution system, followed by solid-liquid separation to obtain copper cobalt methanesulfonic acid leaching solution and metal impurity slag; in the methanesulfonic acid solution, The concentration of methanesulfonic acid is 80~150g/L; 步骤(2):将铜钴甲磺酸浸出液进行电置换处理,分离得到海绵铜和脱铜钴液;其中,电置换过程中的电流密度为10~30mA/cm2Step (2): subjecting the copper-cobalt methanesulfonic acid leaching solution to electro-replacement treatment to separate the sponge copper and the copper-removed cobalt solution; wherein, the current density in the electro-replacement process is 10-30 mA/cm 2 . 2.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,所述的铜钴渣为含有铜、钴以及金属杂质元素;所述的金属杂质元素为包含铁、铅、锑中的至少一种。2. the method for recovering copper and cobalt from copper-cobalt slag as claimed in claim 1, is characterized in that, described copper-cobalt slag contains copper, cobalt and metal impurity elements; Described metal impurity element is to contain iron , at least one of lead and antimony. 3.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,所述的铜钴渣中,含铜10%~30%,含钴1%~10%,各金属杂质的含量均不高于5%。3. the method for recovering copper and cobalt from copper-cobalt slag as claimed in claim 1, is characterized in that, in described copper-cobalt slag, copper-containing 10%~30%, cobalt-containing 1%~10%, each The content of metal impurities is not higher than 5%. 4.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,所述的甲磺酸溶液中,甲磺酸的浓度为80~120g/L。4. the method for reclaiming copper, cobalt from copper-cobalt slag as claimed in claim 1, is characterized in that, in described methanesulfonic acid solution, the concentration of methanesulfonic acid is 80~120g/L. 5.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,铜钴渣与甲磺酸溶液的固液质量比为1:4~8。5. the method for reclaiming copper, cobalt from copper-cobalt slag as claimed in claim 1, is characterized in that, the solid-liquid mass ratio of copper-cobalt slag and methanesulfonic acid solution is 1:4~8. 6.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,所述的氧化剂为双氧水。6. The method for recovering copper and cobalt from copper-cobalt slag as claimed in claim 1, wherein the oxidant is hydrogen peroxide. 7.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,选择性氧化浸出过程的温度为30~90℃。7. The method for recovering copper and cobalt from copper-cobalt slag as claimed in claim 1, wherein the temperature of the selective oxidation leaching process is 30 to 90°C. 8.如权利要求7所述的从铜钴渣中回收铜、钴的方法,其特征在于,浸出时间为0.5~3h。8. the method for recovering copper, cobalt from copper-cobalt slag as claimed in claim 7, is characterized in that, leaching time is 0.5~3h. 9.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,步骤(2)中,采用铜钴甲磺酸浸出液为置换原液;以金属板为阳极,惰性电极为阴极,浸入置换原液中,通电进行电置换;9. the method for reclaiming copper, cobalt from copper-cobalt slag as claimed in claim 1, is characterized in that, in step (2), adopts copper-cobalt methanesulfonic acid leaching solution as replacement stock solution; Taking metal plate as anode, inert electrode It is the cathode, which is immersed in the replacement stock solution and electrified for electrical replacement; 金属板为锌和/或铁;The metal sheet is zinc and/or iron; 惰性阴极为石墨、钛网或不锈钢板;The inert cathode is graphite, titanium mesh or stainless steel plate; 阴阳极板面积比为1:1;The area ratio of cathode and anode plates is 1:1; 极板间距为2~5 cm。The distance between the plates is 2 to 5 cm. 10.如权利要求1或9所述的从铜钴渣中回收铜、钴的方法,其特征在于,步骤(2)中,控制铜钴甲磺酸浸出液中甲磺酸的浓度为20~80g/L。10. the method for reclaiming copper, cobalt from copper-cobalt slag as claimed in claim 1 or 9, is characterized in that, in step (2), the concentration of methanesulfonic acid in the control copper-cobalt methanesulfonic acid leaching solution is 20~80g /L. 11.如权利要求10所述的从铜钴渣中回收铜、钴的方法,其特征在于,步骤(2)中,控制铜钴甲磺酸浸出液中甲磺酸的浓度为30~70g/L。11. the method for reclaiming copper, cobalt from copper-cobalt slag as claimed in claim 10, is characterized in that, in step (2), the concentration of methanesulfonic acid in the control copper-cobalt methanesulfonic acid leachate is 30~70g/L . 12.如权利要求1或9所述的从铜钴渣中回收铜、钴的方法,其特征在于,步骤(2)中,电置换起始溶液的pH为0.2~3。12. The method for recovering copper and cobalt from copper-cobalt slag as claimed in claim 1 or 9, wherein in step (2), the pH of the electro-displacement starting solution is 0.2 to 3. 13.如权利要求1或9所述的从铜钴渣中回收铜、钴的方法,其特征在于,电置换过程中的电流密度为10~20mA/cm213. The method for recovering copper and cobalt from copper-cobalt slag according to claim 1 or 9, characterized in that the current density in the electric displacement process is 10-20 mA/cm 2 . 14.如权利要求13所述的从铜钴渣中回收铜、钴的方法,其特征在于,电置换过程中的电流密度为15~20mA/cm214 . The method for recovering copper and cobalt from copper-cobalt slag according to claim 13 , wherein the current density in the electric displacement process is 15-20 mA/cm 2 . 15.如权利要求1或9所述的从铜钴渣中回收铜、钴的方法,其特征在于,电置换过程的温度为30~80℃。15. The method for recovering copper and cobalt from copper-cobalt slag as claimed in claim 1 or 9, characterized in that the temperature of the electric displacement process is 30-80°C. 16.如权利要求1所述的从铜钴渣中回收铜、钴的方法,其特征在于,将获得的脱铜钴液与草酸发生沉淀反应,随后经煅烧处理,得到Co3O416 . The method for recovering copper and cobalt from copper-cobalt slag as claimed in claim 1 , wherein the obtained copper-removing cobalt solution is subjected to a precipitation reaction with oxalic acid, followed by calcination to obtain Co 3 O 4 . 17 .
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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4322390A (en) * 1980-10-27 1982-03-30 Uop Inc. Hydrometallurgical recovery of copper, cobalt nickel with reductive and oxidative leaching
US4650553A (en) * 1986-03-21 1987-03-17 Pennwalt Corporation Electrolytic recovery of lead from scrap
CN104039991A (en) * 2012-11-13 2014-09-10 巴斯夫欧洲公司 Recovering lead from a mixed oxidized material
CN106222430A (en) * 2016-08-04 2016-12-14 西北矿冶研究院 Method for recovering copper and cobalt from copper-cobalt slag by wet metallurgy
WO2019121086A1 (en) * 2017-12-19 2019-06-27 Basf Se Battery recycling by treatment of the leach with metallic nickel
CN110923468A (en) * 2019-12-02 2020-03-27 赵坤 Method for recovering metallic lead from lead-containing materials such as lead sulfate slag

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EA201790894A1 (en) * 2014-10-22 2017-08-31 Инновеко Острелия Пти. Лтд. METHOD OF METAL EXTRACTION BY MEANS OF SORPTION LEACHING IN WET SOLID MATERIALS

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4322390A (en) * 1980-10-27 1982-03-30 Uop Inc. Hydrometallurgical recovery of copper, cobalt nickel with reductive and oxidative leaching
US4650553A (en) * 1986-03-21 1987-03-17 Pennwalt Corporation Electrolytic recovery of lead from scrap
CN104039991A (en) * 2012-11-13 2014-09-10 巴斯夫欧洲公司 Recovering lead from a mixed oxidized material
CN106222430A (en) * 2016-08-04 2016-12-14 西北矿冶研究院 Method for recovering copper and cobalt from copper-cobalt slag by wet metallurgy
WO2019121086A1 (en) * 2017-12-19 2019-06-27 Basf Se Battery recycling by treatment of the leach with metallic nickel
CN110923468A (en) * 2019-12-02 2020-03-27 赵坤 Method for recovering metallic lead from lead-containing materials such as lead sulfate slag

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