CN115418486B - Method for jointly recovering cobalt and manganese in zinc purification slag by acid leaching-precipitation flotation method - Google Patents
Method for jointly recovering cobalt and manganese in zinc purification slag by acid leaching-precipitation flotation method Download PDFInfo
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- 239000011572 manganese Substances 0.000 title claims abstract description 64
- 229910052748 manganese Inorganic materials 0.000 title claims abstract description 62
- 229910017052 cobalt Inorganic materials 0.000 title claims abstract description 56
- 239000010941 cobalt Substances 0.000 title claims abstract description 56
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 title claims abstract description 55
- 238000005188 flotation Methods 0.000 title claims abstract description 46
- 239000011701 zinc Substances 0.000 title claims abstract description 39
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 title claims abstract description 38
- 229910052725 zinc Inorganic materials 0.000 title claims abstract description 38
- 239000002253 acid Substances 0.000 title claims abstract description 36
- 238000000034 method Methods 0.000 title claims abstract description 34
- 238000001556 precipitation Methods 0.000 title claims abstract description 34
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 title claims abstract description 32
- 238000000746 purification Methods 0.000 title claims abstract description 19
- 239000002893 slag Substances 0.000 title claims abstract description 18
- 238000002386 leaching Methods 0.000 claims abstract description 113
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 58
- 239000004094 surface-active agent Substances 0.000 claims abstract description 19
- MZZUATUOLXMCEY-UHFFFAOYSA-N cobalt manganese Chemical compound [Mn].[Co] MZZUATUOLXMCEY-UHFFFAOYSA-N 0.000 claims abstract description 13
- 230000009467 reduction Effects 0.000 claims abstract description 10
- 230000002378 acidificating effect Effects 0.000 claims abstract description 8
- 230000001376 precipitating effect Effects 0.000 claims abstract description 3
- 239000003795 chemical substances by application Substances 0.000 claims description 33
- 238000006243 chemical reaction Methods 0.000 claims description 22
- 239000007787 solid Substances 0.000 claims description 22
- 239000006260 foam Substances 0.000 claims description 19
- 239000003638 chemical reducing agent Substances 0.000 claims description 16
- 239000007788 liquid Substances 0.000 claims description 14
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 claims description 9
- YXAOOTNFFAQIPZ-UHFFFAOYSA-N 1-nitrosonaphthalen-2-ol Chemical compound C1=CC=CC2=C(N=O)C(O)=CC=C21 YXAOOTNFFAQIPZ-UHFFFAOYSA-N 0.000 claims description 8
- LZZYPRNAOMGNLH-UHFFFAOYSA-M Cetrimonium bromide Chemical group [Br-].CCCCCCCCCCCCCCCC[N+](C)(C)C LZZYPRNAOMGNLH-UHFFFAOYSA-M 0.000 claims description 8
- 229920002401 polyacrylamide Polymers 0.000 claims description 8
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 6
- 238000003723 Smelting Methods 0.000 claims description 6
- 229910001429 cobalt ion Inorganic materials 0.000 claims description 6
- XLJKHNWPARRRJB-UHFFFAOYSA-N cobalt(2+) Chemical compound [Co+2] XLJKHNWPARRRJB-UHFFFAOYSA-N 0.000 claims description 6
- 239000002244 precipitate Substances 0.000 claims description 5
- 238000004062 sedimentation Methods 0.000 claims description 4
- CZMRCDWAGMRECN-UGDNZRGBSA-N Sucrose Chemical compound O[C@H]1[C@H](O)[C@@H](CO)O[C@@]1(CO)O[C@@H]1[C@H](O)[C@@H](O)[C@H](O)[C@@H](CO)O1 CZMRCDWAGMRECN-UGDNZRGBSA-N 0.000 claims description 3
- 229930006000 Sucrose Natural products 0.000 claims description 3
- 239000005720 sucrose Substances 0.000 claims description 3
- 238000000926 separation method Methods 0.000 abstract description 27
- 238000011084 recovery Methods 0.000 abstract description 13
- 230000008569 process Effects 0.000 abstract description 10
- 238000009854 hydrometallurgy Methods 0.000 abstract description 5
- 230000007613 environmental effect Effects 0.000 abstract description 3
- 230000003311 flocculating effect Effects 0.000 abstract 1
- 238000009291 froth flotation Methods 0.000 abstract 1
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 18
- 239000002245 particle Substances 0.000 description 18
- 238000010907 mechanical stirring Methods 0.000 description 14
- 238000003756 stirring Methods 0.000 description 12
- 238000003828 vacuum filtration Methods 0.000 description 12
- 229910052751 metal Inorganic materials 0.000 description 10
- 239000002184 metal Substances 0.000 description 10
- 150000002739 metals Chemical class 0.000 description 9
- 238000003760 magnetic stirring Methods 0.000 description 7
- 239000000047 product Substances 0.000 description 7
- 230000002829 reductive effect Effects 0.000 description 7
- 238000002474 experimental method Methods 0.000 description 6
- 239000000203 mixture Substances 0.000 description 6
- 230000007935 neutral effect Effects 0.000 description 6
- 238000012546 transfer Methods 0.000 description 6
- 239000003153 chemical reaction reagent Substances 0.000 description 4
- 230000002411 adverse Effects 0.000 description 3
- 230000000052 comparative effect Effects 0.000 description 3
- 230000001276 controlling effect Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000008394 flocculating agent Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- SSHIVHKMGVBXTJ-UHFFFAOYSA-N 1-nitronaphthalen-2-ol Chemical compound C1=CC=CC2=C([N+]([O-])=O)C(O)=CC=C21 SSHIVHKMGVBXTJ-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 238000000638 solvent extraction Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- KJCVRFUGPWSIIH-UHFFFAOYSA-N 1-naphthol Chemical compound C1=CC=C2C(O)=CC=CC2=C1 KJCVRFUGPWSIIH-UHFFFAOYSA-N 0.000 description 1
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 1
- 229910019142 PO4 Inorganic materials 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000009713 electroplating Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- ZOOODBUHSVUZEM-UHFFFAOYSA-N ethoxymethanedithioic acid Chemical compound CCOC(S)=S ZOOODBUHSVUZEM-UHFFFAOYSA-N 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 230000008676 import Effects 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 229910001437 manganese ion Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000010452 phosphate Substances 0.000 description 1
- 125000002467 phosphate group Chemical class [H]OP(=O)(O[H])O[*] 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 239000012991 xanthate Substances 0.000 description 1
Classifications
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- 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
- C22B7/006—Wet processes
- C22B7/007—Wet processes by acid leaching
-
- 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
- C22B19/00—Obtaining zinc or zinc oxide
- C22B19/20—Obtaining zinc otherwise than by distilling
- C22B19/22—Obtaining zinc otherwise than by distilling with leaching with acids
-
- 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
- C22B19/00—Obtaining zinc or zinc oxide
- C22B19/30—Obtaining zinc or zinc oxide from metallic residues or scraps
-
- 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
- C22B23/00—Obtaining nickel or cobalt
- C22B23/04—Obtaining nickel or cobalt by wet processes
- C22B23/0407—Leaching processes
- C22B23/0415—Leaching processes with acids or salt solutions except ammonium salts solutions
- C22B23/043—Sulfurated acids or salts thereof
-
- 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
- C22B23/00—Obtaining nickel or cobalt
- C22B23/04—Obtaining nickel or cobalt by wet processes
- C22B23/0453—Treatment or purification of solutions, e.g. obtained by leaching
-
- 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
- C22B23/00—Obtaining nickel or cobalt
- C22B23/04—Obtaining nickel or cobalt by wet processes
- C22B23/0453—Treatment or purification of solutions, e.g. obtained by leaching
- C22B23/0461—Treatment or purification of solutions, e.g. obtained by leaching by chemical methods
-
- 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
- C22B47/00—Obtaining manganese
-
- 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
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- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Manufacturing & Machinery (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
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Abstract
Description
技术领域Technical field
本发明涉及一种湿法炼锌净化渣的处理方法,具体涉及一种酸浸-沉淀浮选法联合回收锌净化渣中钴和锰的方法,属于有色金属冶炼综合回收利用技术领域。The invention relates to a method for processing zinc hydrometallurgy purification slag, specifically to a method for jointly recovering cobalt and manganese from zinc purification slag by an acid leaching-precipitation flotation method, and belongs to the technical field of comprehensive recycling and utilization of non-ferrous metal smelting.
背景技术Background technique
钴及其化合物在新能源材料、特殊性能合金等关键领域有着广泛的应用。随着智能设备和新能源汽车产业的快速发展,钴的需求量将越来越大。我国钴资源以共伴生矿为主,储量仅占世界钴资源储量的1.1%,对钴资源的进口依存度较高。含钴二次资源的回收可以缓解我国钴资源短缺的现状,同时提高资源利用效率,减少传统堆放或焚烧所造成的环境影响。在湿法炼锌过程中,为了消除溶液中钴等杂质金属离子对后续电积步骤的不利影响,需对浸出液进行净化,常用的除钴工艺有锌粉置换、α-亚硝基-β-萘酚除钴、黄药除钴等,同时会产生大量含锌、钴、锰等有价金属的净化渣。净化渣中的锌经处理可循环回收至湿法炼锌系统,其他有价金属经分离富集后也可进行回收利用,具有较高的回收价值。Cobalt and its compounds are widely used in key fields such as new energy materials and special performance alloys. With the rapid development of smart devices and new energy vehicle industries, the demand for cobalt will be increasing. my country's cobalt resources are mainly associated with associated minerals, and their reserves account for only 1.1% of the world's cobalt resource reserves. China is highly dependent on the import of cobalt resources. The recycling of cobalt-containing secondary resources can alleviate the shortage of cobalt resources in my country, while improving resource utilization efficiency and reducing the environmental impact caused by traditional stacking or incineration. In the zinc hydrometallurgy process, in order to eliminate the adverse effects of cobalt and other impurity metal ions in the solution on the subsequent electroplating steps, the leachate needs to be purified. Commonly used cobalt removal processes include zinc powder replacement, α-nitroso-β- Cobalt removal with naphthol and cobalt removal with xanthate will also produce a large amount of purification residue containing valuable metals such as zinc, cobalt, and manganese. The zinc in the purified slag can be recycled to the hydro-zinc smelting system after treatment, and other valuable metals can also be recycled after separation and enrichment, which has a high recovery value.
目前,湿法炼锌净化渣的回收主要是通过酸浸或者碱浸,将全部或者一部分有价金属溶解到溶液中,在溶液中进行分离富集。常用的分离方法有氢氧化物沉淀法、硫化沉淀法、氧化沉淀法、溶剂萃取法等,但由于各种沉淀法实施过程中沉淀容易互相夹带,难以进行深度分离,溶剂萃取法虽分离效果较好,但萃取剂使用成本较高。对于所含有价金属种类较多的净化钴渣,单一的分离方法通常无法做到对全部有价金属的富集回收,需要采用联合工艺逐步分离富集。At present, the recovery of zinc hydrometallurgy purification residue is mainly through acid leaching or alkali leaching, dissolving all or part of the valuable metals into the solution, and performing separation and enrichment in the solution. Commonly used separation methods include hydroxide precipitation, sulfide precipitation, oxidation precipitation, solvent extraction, etc. However, since the precipitates are easily entrained with each other during the implementation of various precipitation methods, it is difficult to perform deep separation. Although the solvent extraction method has a better separation effect Good, but the cost of using the extraction agent is higher. For purified cobalt slag that contains many types of valuable metals, a single separation method usually cannot enrich and recover all valuable metals, and a combined process needs to be used to gradually separate and enrich it.
发明内容Contents of the invention
基于现有湿法炼锌净化渣回收技术中存在的对有价金属选择性差、分离效率低且分离不彻底的缺陷,本发明的目的是在于提供一种酸浸-沉淀浮选法联合回收锌净化渣中钴和锰的方法。该方法采用选择性酸浸-还原酸浸-沉淀浮选联合工艺,得到富钴泡沫产品和富集锰溶液,其工艺流程短,处理成本低,可实现净化钴渣的绿色高值利用。Based on the defects of poor selectivity of valuable metals, low separation efficiency and incomplete separation existing in the existing hydrometallurgical zinc purification slag recovery technology, the purpose of the present invention is to provide a combined acid leaching-precipitation flotation method to recover zinc. Method for purifying cobalt and manganese in slag. This method uses a combined process of selective acid leaching-reducing acid leaching-sedimentation flotation to obtain cobalt-rich foam products and manganese-enriched solutions. The process is short, the treatment cost is low, and it can achieve green and high-value utilization of purified cobalt slag.
为了实现上述目的,本发明提供了一种酸浸-沉淀浮选法联合回收锌净化渣中钴和锰的方法,其包括以下步骤:In order to achieve the above object, the present invention provides a method for jointly recovering cobalt and manganese in zinc purification residue by acid leaching and precipitation flotation, which includes the following steps:
1)将锌冶炼净化渣采用硫酸浸出,得到浸出液和浸出渣;1) Leach the zinc smelting purification residue with sulfuric acid to obtain leachate and leaching residue;
2)将所述浸出渣通过酸性还原浸出,得到钴锰浸出液;2) Leaching the leaching residue through acidic reduction to obtain cobalt and manganese leaching liquid;
3)将所述钴锰浸出液依次进行沉淀和絮凝,再加入表面活性剂进行泡沫浮选,收集富钴泡沫和富锰溶液。3) Precipitate and flocculate the cobalt-manganese leachate in sequence, then add surfactant to perform foam flotation, and collect cobalt-rich foam and manganese-rich solution.
本发明通过选择性酸浸法-还原酸浸-沉淀浮选联合工艺,可逐步富集回收净化渣中钴、锰和锌这三种有价金属,操作简单,可控性强,其中,各步骤中的反应原理如下:The present invention can gradually enrich and recover the three valuable metals of cobalt, manganese and zinc in the purified residue through the combined process of selective acid leaching-reductive acid leaching-precipitation flotation. It is simple to operate and has strong controllability. Among them, each The reaction principle in the steps is as follows:
硫酸浸出:Zn+H2SO4=ZnSO4+H2 Sulfuric acid leaching: Zn+H 2 SO 4 =ZnSO 4 +H 2
ZnO+H2SO4=ZnSO4+H2OZnO+H 2 SO 4 =ZnSO 4 +H 2 O
CoO+H2SO4=CoSO4+H2OCoO+H 2 SO 4 =CoSO 4 +H 2 O
还原酸浸:MnO2+H2SO4+H2O2=MnSO4+2H2O+O2↑Reductive acid leaching: MnO 2 +H 2 SO 4 +H 2 O 2 =MnSO 4 +2H 2 O+O 2 ↑
Co2O3+2H2SO4+H2O2=2CoSO4+3H2O+O2↑Co 2 O 3 +2H 2 SO 4 +H 2 O 2 =2CoSO 4 +3H 2 O+O 2 ↑
沉淀浮选:CoSO4+Na2S=CoS+Na2SO4 Sedimentation flotation: CoSO 4 +Na 2 S=CoS+Na 2 SO 4
Co3++3C10H6ONOH=CO(C10H6ONO)3↓+3H+ Co 3+ +3C 10 H 6 ONOH=CO(C 10 H 6 ONO) 3 ↓+3H +
作为一个优选的方案,步骤1)中,所述浸出的条件为:硫酸浓度为2~4mol/L,液固比为10~20mL:1g,温度为20~40℃,时间为10~30min。所述浸出过程采用转速为200~400rpm的机械搅拌辅助浸出。所述含钴颗粒悬浮液转移至微泡浮选柱中进行充气浮选。As a preferred solution, in step 1), the leaching conditions are: sulfuric acid concentration is 2 to 4 mol/L, liquid-to-solid ratio is 10 to 20 mL: 1 g, temperature is 20 to 40°C, and time is 10 to 30 minutes. The leaching process uses mechanical stirring with a rotation speed of 200 to 400 rpm to assist leaching. The cobalt-containing particle suspension is transferred to a microbubble flotation column for aeration flotation.
该浸出反应过程中,需控制硫酸浓度、液固比在合适的范围,其中,硫酸浓度或液固比过低会导致锌的浸出率较低,无法实现选择性浸出;硫酸浓度过高会造成试剂的浪费,而液固比过高会减低锌的富集程度。反应温度和时间同样影响浸出效率,温度过高或反应时间过长会导致钴的浸出率增大,使得浸出渣中的钴减少。During the leaching reaction process, it is necessary to control the sulfuric acid concentration and liquid-to-solid ratio within appropriate ranges. If the sulfuric acid concentration or liquid-to-solid ratio is too low, the leaching rate of zinc will be low and selective leaching cannot be achieved; if the sulfuric acid concentration is too high, it will cause Waste of reagents, and too high liquid-to-solid ratio will reduce the degree of zinc enrichment. Reaction temperature and time also affect the leaching efficiency. Too high temperature or too long reaction time will increase the leaching rate of cobalt and reduce the cobalt in the leaching residue.
作为一个优选的方案,所述酸性还原浸出采用包含硫酸和还原剂的浸出剂。所述还原剂为双氧水、蔗糖、柠檬酸中至少一种。采用双氧水、蔗糖、柠檬酸等作为还原剂,可将Co3+还原为Co2+,Mn4+还原为Mn2+,从而使钴和锰溶解在溶液中,便于后续钴锰分离。As a preferred solution, the acidic reduction leaching uses a leaching agent containing sulfuric acid and a reducing agent. The reducing agent is at least one of hydrogen peroxide, sucrose and citric acid. Using hydrogen peroxide, sucrose, citric acid, etc. as reducing agents can reduce Co 3+ to Co 2+ and Mn 4+ to Mn 2+ , thereby dissolving cobalt and manganese in the solution to facilitate subsequent cobalt and manganese separation.
作为一个优选的方案,步骤2)中,所述酸性还原浸出的条件为:所述浸出剂中硫酸浓度为0.6~1.4mol/L,还原剂浓度为0.8~1.2mol/L,液固比为8~12mL:1g。As a preferred solution, in step 2), the conditions for the acidic reduction leaching are: the sulfuric acid concentration in the leaching agent is 0.6~1.4mol/L, the reducing agent concentration is 0.8~1.2mol/L, and the liquid-to-solid ratio is 8~12mL: 1g.
作为一个优选的方案,步骤2)中,所述酸性还原浸出的条件为:温度为20~40℃,时间为10~30min。将所述浸出渣采用还原酸溶液浸出时,采用转速为200~400rpm的机械搅拌辅助浸出。As a preferred solution, in step 2), the acidic reduction leaching conditions are: temperature is 20-40°C, and time is 10-30 minutes. When the leaching residue is leached with a reducing acid solution, mechanical stirring with a rotation speed of 200 to 400 rpm is used to assist the leaching.
在该还原浸出反应过程中,控制硫酸浓度、还原剂浓度(添加量)和液固比在合适的范围能够提高选择性浸出效率。硫酸浓度浓度、还原剂浓度(添加量)或液固比过低,均会导致钴锰的浸出率较低;硫酸浓度或还原剂浓度(添加量)过高会导致试剂的浪费,提高生产成本,而液固比过高则会减低钴和锰的富集程度。During the reduction leaching reaction process, controlling the sulfuric acid concentration, reducing agent concentration (added amount) and liquid-to-solid ratio within appropriate ranges can improve the selective leaching efficiency. Too low sulfuric acid concentration, reducing agent concentration (added amount) or liquid-to-solid ratio will result in low cobalt and manganese leaching rate; too high sulfuric acid concentration or reducing agent concentration (added amount) will lead to waste of reagents and increase production costs. , and too high a liquid-to-solid ratio will reduce the enrichment of cobalt and manganese.
作为一个优选的方案,所述沉淀剂为药剂A,所述药剂A包含α-亚硝基-β-萘酚和Na2S,α-亚硝基-β-萘酚与Na2S的摩尔比为1~3:1。所述沉淀剂用量为溶液中钴离子摩尔量的0.8~1.2倍。As a preferred solution, the precipitating agent is agent A, which contains α-nitroso-β-naphthol and Na 2 S, and the mole ratio of α-nitroso-β-naphthol to Na 2 S The ratio is 1~3:1. The dosage of the precipitant is 0.8 to 1.2 times the molar amount of cobalt ions in the solution.
采用上述沉淀剂组分可选择性沉淀溶液中的钴离子。在该选择性沉淀反应过程中,需要控制沉淀剂用量在合适的范围,沉淀剂用量过少会导致钴离子沉淀反应不完全,沉淀剂用量过多则会导致过量的沉淀剂与锰反应生成沉淀,无法实现选择性沉淀。The above precipitant components can be used to selectively precipitate cobalt ions in the solution. In this selective precipitation reaction process, the amount of precipitant needs to be controlled within an appropriate range. Too little amount of precipitant will lead to incomplete cobalt ion precipitation reaction, and too much amount of precipitant will cause excess precipitant to react with manganese to form precipitation. , unable to achieve selective precipitation.
作为一个优选的方案,所述絮凝剂为聚丙烯酰胺。所述絮凝剂在溶液中的浓度为10~100mg/L。在絮凝过程中,采用转速为200~400rpm的磁力搅拌辅助浸出。As a preferred solution, the flocculant is polyacrylamide. The concentration of the flocculant in the solution is 10-100 mg/L. During the flocculation process, magnetic stirring with a rotation speed of 200 to 400 rpm is used to assist leaching.
采用絮凝剂可使钴沉淀颗粒聚集,同时控制絮凝剂在合适的范围可提高后续浮选分离效率。如果絮凝剂加入量过少(浓度过低)会导致沉淀物颗粒无法聚集,对后续浮选回收率造成不利影响;如果絮凝剂加入量过多(浓度过高)会造成试剂的浪费,提高生产成本。The use of flocculants can aggregate cobalt precipitated particles, and controlling the flocculants in a suitable range can improve the efficiency of subsequent flotation separation. If the amount of flocculant added is too small (the concentration is too low), the sediment particles will not be able to aggregate, which will adversely affect the subsequent flotation recovery rate; if the amount of flocculant added is too much (the concentration is too high), it will cause waste of reagents and increase production. cost.
作为一个优选的方案,所述表面活性剂为CTAB。所述表面活性剂在溶液中的浓度为10~50mg/L。As a preferred solution, the surfactant is CTAB. The concentration of the surfactant in the solution is 10-50 mg/L.
通过添加表面活性剂能够增强泡沫稳定性,提高颗粒可浮性。调控溶液中表面活性剂浓度在合适的范围有利于钴锰的高效分离,表面活性剂加入量过少(浓度过低)会导致颗粒可浮性较弱,影响浮选回收率;而表面活性剂加入量过多(浓度过高)则会造成溶液中表面活性剂的残留,影响分离效率。Adding surfactants can enhance foam stability and improve particle floatability. Regulating the concentration of surfactant in the solution within a suitable range is beneficial to the efficient separation of cobalt and manganese. Adding too little surfactant (concentration is too low) will result in weak floatability of the particles and affect the flotation recovery rate; while surfactant Adding too much (too high a concentration) will cause surfactant residues in the solution and affect the separation efficiency.
作为一个优选的方案,步骤3)中,所述沉淀反应条件为:溶液体系的pH为2~4。温度为20~40℃,时间为10~30min。As a preferred option, in step 3), the precipitation reaction conditions are: the pH of the solution system is 2-4. The temperature is 20~40℃ and the time is 10~30min.
在该选择性沉淀反应过程中,控制溶液体系的pH在合适的范围有利于钴锰的高效分离回收,溶液体系的pH值过高会造成钴离子和锰离子水解沉淀,而溶液体系的pH值过低则会对后续沉淀浮选反应造成不利影响。During the selective precipitation reaction process, controlling the pH of the solution system within a suitable range is conducive to the efficient separation and recovery of cobalt and manganese. Too high a pH value of the solution system will cause hydrolysis and precipitation of cobalt ions and manganese ions, and the pH value of the solution system If it is too low, it will have an adverse effect on the subsequent sedimentation and flotation reaction.
与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:
(1)该方法中首先采用硫酸选择性浸出锌,使得95%以上的锌浸出至浸出液中,浸出液可返回湿法炼锌主系统回收锌;其次通过酸还原浸出得到富钴锰浸出液,通过加入特定的沉淀剂选择性沉淀钴离子,通过加入絮凝剂和表面活性剂使含钴沉淀颗粒和富锰溶液经泡沫浮选后完全分离,逐步实现了净化渣中锌钴锰的高效分离和高值回收。(1) In this method, zinc is first selectively leached using sulfuric acid, so that more than 95% of the zinc is leached into the leachate, and the leachate can be returned to the main wet zinc smelting system to recover zinc; secondly, cobalt-rich manganese leachate is obtained through acid reduction leaching, and the leachate is added A specific precipitant selectively precipitates cobalt ions, and by adding flocculants and surfactants, the cobalt-containing precipitated particles and manganese-rich solution are completely separated after foam flotation, gradually achieving efficient separation and high value of zinc, cobalt, and manganese in the purification slag. Recycle.
(2)该方法工艺流程短,操作难度低,技术条件易控制,对环境友好,与湿法炼锌主系统适应性强,具有较好的产业化应用前景。(2) This method has a short process flow, low operating difficulty, easy control of technical conditions, environmental friendliness, strong adaptability to the main hydrometallurgical zinc smelting system, and good industrial application prospects.
附图说明Description of drawings
图1为本发明的工艺流程示意图。Figure 1 is a schematic diagram of the process flow of the present invention.
具体实施方式Detailed ways
下面结合实施例和附图对本发明作进一步的说明,但不以任何方式对本发明加以限制,基于本发明教导所作的任何变换或替换,均属于本发明的保护范围。The present invention will be further described below with reference to the examples and drawings, but the present invention is not limited in any way. Any transformation or replacement based on the teachings of the present invention falls within the protection scope of the present invention.
除非另有特别说明,本发明中用到的各种原材料、试剂、仪器和设备等均可通过市场购买得到或者可通过现有方法制备得到。Unless otherwise specified, various raw materials, reagents, instruments and equipment used in the present invention can be purchased in the market or prepared by existing methods.
实施例中所用的净化渣的主要化学成分如表1所示:The main chemical components of the purification slag used in the examples are shown in Table 1:
表1净化渣的主要化学成分Table 1 Main chemical components of purification slag
实施例1Example 1
本实施例提供了一种酸浸-沉淀浮选法联合回收锌净化渣中钴和锰的方法,包括以下步骤:This embodiment provides a method for jointly recovering cobalt and manganese in zinc purification residue by acid leaching and precipitation flotation, which includes the following steps:
(1)选择性酸浸:将净化渣破碎、研磨、筛分至粒度小于0.074mm的颗粒质量占比90%以上,获得的样品用于酸浸实验;配置浓度为4mol/L的硫酸浸出剂,与处理好的净化渣按液固比20mL:1g混合,加热至30℃,在300rpm的机械搅拌下浸出10min,通过真空抽滤进行固液分离,得到浸出液和浸出渣。Co、Mn、Zn三种金属的浸出率分别为9.3%、0.1%、96.6%。(1) Selective acid leaching: Crush, grind, and sieve the purified residue until the mass proportion of particles with a particle size less than 0.074mm accounts for more than 90%. The obtained samples are used for acid leaching experiments; configure a sulfuric acid leaching agent with a concentration of 4mol/L , mixed with the treated purified residue at a liquid-to-solid ratio of 20 mL: 1 g, heated to 30°C, leached for 10 minutes under mechanical stirring at 300 rpm, and solid-liquid separation was performed through vacuum filtration to obtain leachate and leaching residue. The leaching rates of Co, Mn, and Zn metals are 9.3%, 0.1%, and 96.6% respectively.
(2)还原酸浸:将步骤(1)中得到的浸出渣洗涤至中性后干燥,配置浓度为1mol/L的硫酸浸出剂,与浸出渣按液固比为10mL:1g混合,加热至30℃,添加还原剂H2O2使其在溶液中的浓度为1mol/L,在300rpm的机械搅拌下浸出20min,通过真空抽滤进行固液分离,Co、Mn的浸出率分别为99.3%、98.7%,得到钴锰溶液。(2) Reductive acid leaching: Wash the leaching residue obtained in step (1) until it is neutral and then dry it. Prepare a sulfuric acid leaching agent with a concentration of 1 mol/L, mix it with the leaching residue at a liquid-to-solid ratio of 10 mL: 1 g, and heat to 30°C, add the reducing agent H 2 O 2 to the solution to a concentration of 1 mol/L, leaching for 20 minutes under mechanical stirring at 300 rpm, and perform solid-liquid separation through vacuum filtration. The leaching rates of Co and Mn are 99.3% respectively. , 98.7%, to obtain a cobalt-manganese solution.
(3)沉淀反应:将步骤(2)中得到的钴锰溶液用NaOH溶液调节至pH为3,加入与钴反应理论反应量1.2倍的药剂A,且该药剂A由摩尔比为1:1的α-亚硝基-β-萘酚与Na2S组成;加热至30℃,在300rpm的磁力搅拌下反应10min,Co、Mn的沉淀率分别为96.3%、5.4%。随后加入絮凝剂聚丙烯酰胺,使其在溶液中的浓度为50mg/L,搅拌均匀后,加入表面活性剂CTAB,使其在溶液中的浓度为50mg/L,并搅拌均匀。(3) Precipitation reaction: Adjust the cobalt and manganese solution obtained in step (2) to pH 3 with NaOH solution, add agent A that is 1.2 times the theoretical reaction amount with cobalt, and the molar ratio of agent A is 1:1 Composed of α-nitroso-β-naphthol and Na 2 S; heated to 30°C and reacted for 10 minutes under magnetic stirring at 300 rpm. The precipitation rates of Co and Mn were 96.3% and 5.4% respectively. Then add the flocculant polyacrylamide so that the concentration in the solution is 50 mg/L. After stirring evenly, add the surfactant CTAB so that the concentration in the solution is 50 mg/L and stir evenly.
(4)泡沫浮选:将步骤(3)中得到的溶液体系转移至微泡浮选柱中进行充气浮选,收集富钴泡沫产品和富集锰溶液,Co、Mn的浮选回收率分别为92.5%、2.7%。(4) Foam flotation: Transfer the solution system obtained in step (3) to a microbubble flotation column for air-filled flotation to collect cobalt-rich foam products and manganese-rich solutions. The flotation recovery rates of Co and Mn are respectively 92.5%, 2.7%.
实施例2Example 2
(1)选择性酸浸:将净化渣破碎、研磨、筛分至粒度小于0.074mm的颗粒质量占比90%以上,获得的样品用于酸浸实验;配置浓度为2mol/L的硫酸浸出剂,与处理好的净化渣按液固比10mL:1g混合,加热至40℃,在300rpm的机械搅拌下浸出20min,通过真空抽滤进行固液分离,得到浸出液和浸出渣。Co、Mn、Zn三种金属的浸出率分别为8.9%、0.1%、93.4%。(1) Selective acid leaching: Crush, grind, and screen the purified residue until the mass proportion of particles with a particle size less than 0.074 mm accounts for more than 90%. The obtained samples are used for acid leaching experiments; configure a sulfuric acid leach agent with a concentration of 2 mol/L , mixed with the treated purified residue at a liquid-to-solid ratio of 10 mL: 1 g, heated to 40°C, leached for 20 minutes under mechanical stirring at 300 rpm, and solid-liquid separation was performed through vacuum filtration to obtain leachate and leaching residue. The leaching rates of Co, Mn and Zn are 8.9%, 0.1% and 93.4% respectively.
(2)还原酸浸:将步骤(1)中得到的浸出渣洗涤至中性后干燥,配置浓度为0.8mol/L的硫酸浸出剂,与浸出渣按液固比为8mL:1g混合,加热至40℃,添加还原剂H2O2使其在溶液中的浓度为0.8mol/L,在300rpm的机械搅拌下浸出30min,通过真空抽滤进行固液分离,Co、Mn的浸出率分别为98.6%、98.1%,得到钴锰溶液。(2) Reductive acid leaching: Wash the leaching residue obtained in step (1) until it is neutral and then dry it. Prepare a sulfuric acid leaching agent with a concentration of 0.8 mol/L, mix it with the leaching residue at a liquid-to-solid ratio of 8 mL: 1 g, and heat to 40°C, add the reducing agent H 2 O 2 so that the concentration in the solution is 0.8 mol/L, leaching for 30 minutes under mechanical stirring at 300 rpm, and perform solid-liquid separation through vacuum filtration. The leaching rates of Co and Mn are respectively 98.6%, 98.1%, and a cobalt-manganese solution was obtained.
(3)沉淀反应:将步骤(2)中得到的钴锰溶液用NaOH溶液调节至pH为2.5,加入理论反应量1倍的药剂A,且该药剂A由摩尔比为3:1的α-亚硝基-β-萘酚与Na2S组成;加热至40℃,在300rpm的磁力搅拌下反应20min,Co、Mn的沉淀率分别为95.2%、3.5%。随后加入絮凝剂聚丙烯酰胺,使其在溶液中浓度为30mg/L,搅拌均匀后,加入表面活性剂CTAB,使其在溶液中的浓度为30mg/L,并搅拌均匀。(3) Precipitation reaction: Adjust the cobalt-manganese solution obtained in step (2) to pH 2.5 with NaOH solution, add agent A that is 1 times the theoretical reaction amount, and the agent A is composed of α- Nitroso-β-naphthol is composed of Na 2 S; heated to 40°C and reacted for 20 minutes under magnetic stirring at 300 rpm. The precipitation rates of Co and Mn were 95.2% and 3.5% respectively. Then add the flocculant polyacrylamide so that the concentration in the solution is 30 mg/L. After stirring evenly, add the surfactant CTAB so that the concentration in the solution is 30 mg/L and stir evenly.
(4)泡沫浮选:将步骤(3)中得到的溶液体系转移至微泡浮选柱中进行充气浮选,收集富钴泡沫产品和富集锰溶液,Co、Mn的浮选回收率分别为92.3%、2.4%。(4) Foam flotation: Transfer the solution system obtained in step (3) to a microbubble flotation column for air-filled flotation to collect cobalt-rich foam products and manganese-rich solutions. The flotation recovery rates of Co and Mn are respectively 92.3%, 2.4%.
实施例3Example 3
(1)选择性酸浸:将净化渣破碎、研磨、筛分至粒度小于0.074mm的颗粒质量占比90%以上,获得的样品用于酸浸实验;配置浓度为2mol/L的硫酸浸出剂,与处理好的净化渣按液固比15mL:1g混合,加热至35℃,在300rpm的机械搅拌下浸出15min,通过真空抽滤进行固液分离,得到浸出液和浸出渣。Co、Mn、Zn三种金属的浸出率分别为9.1%、0.1%、95.8%。(1) Selective acid leaching: Crush, grind, and screen the purified residue until the mass proportion of particles with a particle size less than 0.074 mm accounts for more than 90%. The obtained samples are used for acid leaching experiments; configure a sulfuric acid leach agent with a concentration of 2 mol/L , mixed with the treated purified residue at a liquid-to-solid ratio of 15 mL: 1 g, heated to 35°C, leached for 15 minutes under mechanical stirring at 300 rpm, and solid-liquid separation was performed through vacuum filtration to obtain leachate and leaching residue. The leaching rates of Co, Mn and Zn are 9.1%, 0.1% and 95.8% respectively.
(2)还原酸浸:将步骤(1)中得到的浸出渣洗涤至中性后干燥,配置浓度为1.2mol/L的硫酸浸出剂,与浸出渣按液固比为12mL:1g混合,加热至35℃,添加还原剂H2O2使其在溶液中的浓度为1.2mol/L,在300rpm的机械搅拌下浸出25min,通过真空抽滤进行固液分离,Co、Mn的浸出率分别为99.5%、99.1%,得到钴锰溶液。(2) Reductive acid leaching: Wash the leaching residue obtained in step (1) until it is neutral and then dry it. Prepare a sulfuric acid leaching agent with a concentration of 1.2 mol/L, mix it with the leaching residue at a liquid-to-solid ratio of 12 mL: 1 g, and heat to 35°C, add the reducing agent H 2 O 2 so that the concentration in the solution is 1.2 mol/L, leaching for 25 minutes under mechanical stirring at 300 rpm, and perform solid-liquid separation through vacuum filtration. The leaching rates of Co and Mn are respectively 99.5%, 99.1% to obtain cobalt manganese solution.
(3)沉淀反应:将步骤(2)中得到的钴锰溶液用NaOH溶液调节至pH为3.5,加入理论反应量0.8倍的药剂A,且该药剂A由摩尔比为2:1的α-亚硝基-β-萘酚与Na2S组成;加热至35℃,在300rpm的磁力搅拌下反应15min,Co、Mn的沉淀率分别为94.6%、3.2%。随后加入絮凝剂聚丙烯酰胺,使其在溶液中的浓度为60mg/L,搅拌均匀后,加入表面活性剂CTAB,使其在溶液中的浓度为40mg/L,并搅拌均匀。(3) Precipitation reaction: Adjust the cobalt and manganese solution obtained in step (2) to pH 3.5 with NaOH solution, add agent A with a theoretical reaction amount of 0.8 times, and the agent A is composed of α- at a molar ratio of 2:1 Nitroso-β-naphthol is composed of Na 2 S; heated to 35°C and reacted for 15 minutes under magnetic stirring at 300 rpm. The precipitation rates of Co and Mn were 94.6% and 3.2% respectively. Then add the flocculant polyacrylamide so that the concentration in the solution is 60 mg/L. After stirring evenly, add the surfactant CTAB so that the concentration in the solution is 40 mg/L and stir evenly.
(4)泡沫浮选:将步骤(3)中得到的溶液体系转移至微泡浮选柱中进行充气浮选,收集富钴泡沫产品和富集锰溶液,Co、Mn的浮选回收率分别为91.7%、2.1%。(4) Foam flotation: Transfer the solution system obtained in step (3) to a microbubble flotation column for air-filled flotation to collect cobalt-rich foam products and manganese-rich solutions. The flotation recovery rates of Co and Mn are respectively 91.7%, 2.1%.
对比例1Comparative example 1
(1)选择性酸浸:将净化渣破碎、研磨、筛分至粒度小于0.074mm的颗粒质量占比90%以上,获得的样品用于酸浸实验;配置浓度为4mol/L的硫酸浸出剂,与处理好的净化渣按液固比20mL:1g混合,加热至30℃,在300rpm的机械搅拌下浸出10min,通过真空抽滤进行固液分离,得到浸出液和浸出渣。Co、Mn、Zn三种金属的浸出率分别为9.3%、0.1%、96.6%。(1) Selective acid leaching: Crush, grind, and sieve the purified residue until the mass proportion of particles with a particle size less than 0.074mm accounts for more than 90%. The obtained samples are used for acid leaching experiments; configure a sulfuric acid leaching agent with a concentration of 4mol/L , mixed with the treated purified residue at a liquid-to-solid ratio of 20 mL: 1 g, heated to 30°C, leached for 10 minutes under mechanical stirring at 300 rpm, and solid-liquid separation was performed through vacuum filtration to obtain leachate and leaching residue. The leaching rates of Co, Mn, and Zn metals are 9.3%, 0.1%, and 96.6% respectively.
(2)还原酸浸:将步骤(1)中得到的浸出渣洗涤至中性后干燥,配置浓度为1mol/L的硫酸浸出剂,与浸出渣按液固比为10mL:1g混合,加热至30℃,添加还原剂H2O2使其在溶液中的浓度为0.1mol/L,在300rpm的机械搅拌下浸出20min,通过真空抽滤进行固液分离,Co、Mn的浸出率分别为67.3%、51.7%,得到钴锰溶液。(2) Reductive acid leaching: Wash the leaching residue obtained in step (1) until it is neutral and then dry it. Prepare a sulfuric acid leaching agent with a concentration of 1 mol/L, mix it with the leaching residue at a liquid-to-solid ratio of 10 mL: 1 g, and heat to 30°C, add the reducing agent H 2 O 2 to the solution to a concentration of 0.1 mol/L, leaching for 20 minutes under mechanical stirring at 300 rpm, and perform solid-liquid separation through vacuum filtration. The leaching rates of Co and Mn are 67.3 respectively. %, 51.7%, and a cobalt-manganese solution was obtained.
(3)沉淀反应:将步骤(2)中得到的钴锰溶液用NaOH溶液调节至pH为3,加入理论反应量1.2倍的药剂A,且该药剂A由摩尔比为1:1的α-亚硝基-β-萘酚与Na2S组成;加热至30℃,在300rpm的磁力搅拌下反应10min,Co、Mn的沉淀率分别为97.2%、7.3%。随后加入絮凝剂聚丙烯酰胺,使其在溶液中的浓度为50mg/L,搅拌均匀后,加入表面活性剂CTAB,使其在溶液中的浓度为50mg/L,并搅拌均匀。(3) Precipitation reaction: Adjust the cobalt-manganese solution obtained in step (2) to pH 3 with NaOH solution, add agent A with a theoretical reaction amount of 1.2 times, and the agent A is composed of α- at a molar ratio of 1:1 Nitroso-β-naphthol is composed of Na 2 S; heated to 30°C and reacted for 10 minutes under magnetic stirring at 300 rpm. The precipitation rates of Co and Mn were 97.2% and 7.3% respectively. Then add the flocculant polyacrylamide so that the concentration in the solution is 50 mg/L. After stirring evenly, add the surfactant CTAB so that the concentration in the solution is 50 mg/L and stir evenly.
(4)泡沫浮选:将步骤(3)中得到的溶液体系转移至微泡浮选柱中进行充气浮选,收集富钴泡沫产品和富集锰溶液,Co、Mn的浮选回收率分别为90.2%、4.3%。(4) Foam flotation: Transfer the solution system obtained in step (3) to a microbubble flotation column for air-filled flotation to collect cobalt-rich foam products and manganese-rich solutions. The flotation recovery rates of Co and Mn are respectively 90.2%, 4.3%.
对比例2Comparative example 2
(1)选择性酸浸:将净化渣破碎、研磨、筛分至粒度小于0.074mm的颗粒质量占比90%以上,获得的样品用于酸浸实验;配置浓度为1mol/L的硫酸浸出剂,与处理好的净化渣按液固比10mL:1g混合,加热至40℃,在300rpm的机械搅拌下浸出20min,通过真空抽滤进行固液分离,得到浸出液和浸出渣。Co、Mn、Zn三种金属的浸出率分别为8.9%、0.1%、93.4%。(1) Selective acid leaching: Crush, grind, and screen the purified residue until the mass proportion of particles with a particle size less than 0.074mm accounts for more than 90%. The obtained samples are used for acid leaching experiments; configure a sulfuric acid leaching agent with a concentration of 1 mol/L , mixed with the treated purified residue at a liquid-to-solid ratio of 10 mL: 1 g, heated to 40°C, leached for 20 minutes under mechanical stirring at 300 rpm, and solid-liquid separation was performed through vacuum filtration to obtain leachate and leaching residue. The leaching rates of Co, Mn and Zn are 8.9%, 0.1% and 93.4% respectively.
(2)还原酸浸:将步骤(1)中得到的浸出渣洗涤至中性后干燥,配置浓度为0.8mol/L的硫酸浸出剂,与浸出渣按液固比为8mL:1g混合,加热至40℃,添加还原剂H2O2使其在溶液中的浓度为0.8mol/L,在300rpm的机械搅拌下浸出30min,通过真空抽滤进行固液分离,Co、Mn的浸出率分别为98.6%、98.1%,得到钴锰溶液。(2) Reductive acid leaching: Wash the leaching residue obtained in step (1) until it is neutral and then dry it. Prepare a sulfuric acid leaching agent with a concentration of 0.8 mol/L, mix it with the leaching residue at a liquid-to-solid ratio of 8 mL: 1 g, and heat to 40°C, add the reducing agent H 2 O 2 so that the concentration in the solution is 0.8 mol/L, leaching for 30 minutes under mechanical stirring at 300 rpm, and perform solid-liquid separation through vacuum filtration. The leaching rates of Co and Mn are respectively 98.6%, 98.1%, and a cobalt-manganese solution was obtained.
(3)沉淀反应:将步骤(2)中得到的钴锰溶液用NaOH溶液调节至pH为2.5,加入理论反应量0.5倍的药剂A,且药剂A由摩尔比为3:1的α-亚硝基-β-萘酚与Na2S组成;加热至40℃,在300rpm的磁力搅拌下反应20min,Co、Mn的沉淀率分别为47.3%、0.6%。随后加入絮凝剂聚丙烯酰胺,使其在溶液中的浓度为30mg/L,搅拌均匀后,加入表面活性剂CTAB,使其在溶液中的浓度为30mg/L,并搅拌均匀。(3) Precipitation reaction: Adjust the cobalt-manganese solution obtained in step (2) to pH 2.5 with NaOH solution, add agent A 0.5 times the theoretical reaction amount, and agent A is composed of α-substituted phosphate with a molar ratio of 3:1. Nitro-β-naphthol is composed of Na 2 S; heated to 40°C and reacted for 20 minutes under magnetic stirring at 300 rpm. The precipitation rates of Co and Mn were 47.3% and 0.6% respectively. Then add the flocculant polyacrylamide so that the concentration in the solution is 30 mg/L. After stirring evenly, add the surfactant CTAB so that the concentration in the solution is 30 mg/L and stir evenly.
(4)泡沫浮选:将步骤(3)中得到的溶液体系转移至微泡浮选柱中进行充气浮选,收集富钴泡沫产品和富集锰溶液,Co、Mn的浮选回收率分别为93.4%、2.4%。(4) Foam flotation: Transfer the solution system obtained in step (3) to a microbubble flotation column for air-filled flotation to collect cobalt-rich foam products and manganese-rich solutions. The flotation recovery rates of Co and Mn are respectively 93.4%, 2.4%.
对比例3Comparative example 3
(1)选择性酸浸:将净化渣破碎、研磨、筛分至粒度小于0.074mm的颗粒质量占比90%以上,获得的样品用于酸浸实验;配置浓度为2mol/L的硫酸浸出剂,与处理好的净化渣按液固比15mL:1g混合,加热至35℃,在300rpm的机械搅拌下浸出15min,通过真空抽滤进行固液分离,得到浸出液和浸出渣。Co、Mn、Zn三种金属的浸出率分别为9.1%、0.1%、95.8%。(1) Selective acid leaching: Crush, grind, and screen the purified residue until the mass proportion of particles with a particle size less than 0.074 mm accounts for more than 90%. The obtained samples are used for acid leaching experiments; configure a sulfuric acid leach agent with a concentration of 2 mol/L , mixed with the treated purified residue at a liquid-to-solid ratio of 15 mL: 1 g, heated to 35°C, leached for 15 minutes under mechanical stirring at 300 rpm, and solid-liquid separation was performed through vacuum filtration to obtain leachate and leaching residue. The leaching rates of Co, Mn and Zn are 9.1%, 0.1% and 95.8% respectively.
(2)还原酸浸:将步骤(1)中得到的浸出渣洗涤至中性后干燥,配置浓度为1.2mol/L的硫酸浸出剂,与浸出渣按液固比为12mL:1g混合,加热至35℃,添加还原剂H2O2使其在溶液中的浓度为1.2mol/L,在300rpm的机械搅拌下浸出25min,通过真空抽滤进行固液分离,Co、Mn的浸出率分别为99.5%、99.1%,得到钴锰溶液。(2) Reductive acid leaching: Wash the leaching residue obtained in step (1) until it is neutral and then dry it. Prepare a sulfuric acid leaching agent with a concentration of 1.2 mol/L, mix it with the leaching residue at a liquid-to-solid ratio of 12 mL: 1 g, and heat to 35°C, add the reducing agent H 2 O 2 so that the concentration in the solution is 1.2 mol/L, leaching for 25 minutes under mechanical stirring at 300 rpm, and perform solid-liquid separation through vacuum filtration. The leaching rates of Co and Mn are respectively 99.5%, 99.1% to obtain cobalt manganese solution.
(3)沉淀反应:将步骤(2)中得到的钴锰溶液用NaOH溶液调节至pH为3.5,加入理论反应量0.8倍的药剂A,且药剂A由摩尔比为2:1的α-亚硝基-β-萘酚与Na2S组成;加热至35℃,在300rpm的磁力搅拌下反应15min,Co、Mn的沉淀率分别为94.6%、3.2%。随后加入絮凝剂聚丙烯酰胺,使其在溶液中的浓度为1mg/L,搅拌均匀后,加入表面活性剂CTAB,使其在溶液中的浓度为40mg/L,并搅拌均匀。(3) Precipitation reaction: Adjust the cobalt and manganese solution obtained in step (2) to pH 3.5 with NaOH solution, add agent A with a theoretical reaction amount of 0.8 times, and agent A is composed of α-substituted with a molar ratio of 2:1. Composed of nitro-β-naphthol and Na 2 S; heated to 35°C and reacted for 15 minutes under magnetic stirring at 300 rpm. The precipitation rates of Co and Mn were 94.6% and 3.2% respectively. Then add the flocculant polyacrylamide so that the concentration in the solution is 1 mg/L. After stirring evenly, add the surfactant CTAB so that the concentration in the solution is 40 mg/L and stir evenly.
(4)泡沫浮选:将步骤(3)中得到的溶液体系转移至微泡浮选柱中进行充气浮选,收集富钴泡沫产品和富集锰溶液,Co、Mn的浮选回收率分别为84.2%、1.1%。(4) Foam flotation: Transfer the solution system obtained in step (3) to a microbubble flotation column for air-filled flotation to collect cobalt-rich foam products and manganese-rich solutions. The flotation recovery rates of Co and Mn are respectively 84.2%, 1.1%.
以上结合实施例对本发明的实施方式作了详细说明,但本发明不限于所描述的实施方式。对于本领域的技术人员而言,在不脱离本发明原理和精神的情况下,对这些实施方式进行多种变化、修改、替换和变型,仍落入本发明的保护范围内。The embodiments of the present invention have been described in detail above in conjunction with the examples, but the present invention is not limited to the described embodiments. For those skilled in the art, various changes, modifications, substitutions and modifications can be made to these embodiments without departing from the principle and spirit of the invention, and they still fall within the protection scope of the invention.
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