CN115491499A - Method for separating and recovering strontium from zinc anode mud - Google Patents
Method for separating and recovering strontium from zinc anode mud Download PDFInfo
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- 229910052712 strontium Inorganic materials 0.000 title claims abstract description 107
- CIOAGBVUUVVLOB-UHFFFAOYSA-N strontium atom Chemical compound [Sr] CIOAGBVUUVVLOB-UHFFFAOYSA-N 0.000 title claims abstract description 106
- 239000011701 zinc Substances 0.000 title claims abstract description 41
- 229910052725 zinc Inorganic materials 0.000 title claims abstract description 41
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 title claims abstract description 40
- 238000000034 method Methods 0.000 title claims abstract description 37
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 42
- 238000002386 leaching Methods 0.000 claims abstract description 37
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 claims abstract description 32
- 238000000498 ball milling Methods 0.000 claims abstract description 28
- 238000006243 chemical reaction Methods 0.000 claims abstract description 28
- 239000002253 acid Substances 0.000 claims abstract description 27
- 239000007788 liquid Substances 0.000 claims abstract description 27
- 239000012065 filter cake Substances 0.000 claims abstract description 23
- BDAGIHXWWSANSR-NJFSPNSNSA-N hydroxyformaldehyde Chemical compound O[14CH]=O BDAGIHXWWSANSR-NJFSPNSNSA-N 0.000 claims abstract description 23
- 229910000018 strontium carbonate Inorganic materials 0.000 claims abstract description 23
- 238000000746 purification Methods 0.000 claims abstract description 20
- 238000001556 precipitation Methods 0.000 claims abstract description 12
- 239000000243 solution Substances 0.000 claims description 82
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 22
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 15
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 9
- 239000012535 impurity Substances 0.000 claims description 8
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 claims description 4
- 239000001099 ammonium carbonate Substances 0.000 claims description 4
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 claims description 2
- UIIMBOGNXHQVGW-DEQYMQKBSA-M Sodium bicarbonate-14C Chemical compound [Na+].O[14C]([O-])=O UIIMBOGNXHQVGW-DEQYMQKBSA-M 0.000 claims description 2
- 235000012538 ammonium bicarbonate Nutrition 0.000 claims description 2
- 235000012501 ammonium carbonate Nutrition 0.000 claims description 2
- 239000003795 chemical substances by application Substances 0.000 claims description 2
- 239000012047 saturated solution Substances 0.000 claims description 2
- 235000017550 sodium carbonate Nutrition 0.000 claims description 2
- 150000004649 carbonic acid derivatives Chemical class 0.000 claims 1
- 238000000605 extraction Methods 0.000 claims 1
- 150000002500 ions Chemical class 0.000 claims 1
- 238000011084 recovery Methods 0.000 abstract description 18
- 239000000126 substance Substances 0.000 abstract description 6
- 239000000203 mixture Substances 0.000 description 17
- 239000000047 product Substances 0.000 description 14
- 230000000694 effects Effects 0.000 description 11
- 239000007787 solid Substances 0.000 description 11
- 230000000052 comparative effect Effects 0.000 description 9
- 239000000706 filtrate Substances 0.000 description 8
- 239000000463 material Substances 0.000 description 6
- 238000000926 separation method Methods 0.000 description 5
- 238000004364 calculation method Methods 0.000 description 4
- 239000007795 chemical reaction product Substances 0.000 description 4
- 238000001035 drying Methods 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- 239000002699 waste material Substances 0.000 description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 3
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 229910052791 calcium Inorganic materials 0.000 description 3
- 239000011575 calcium Substances 0.000 description 3
- 238000005363 electrowinning Methods 0.000 description 3
- 239000011133 lead Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000002893 slag Substances 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 238000001994 activation Methods 0.000 description 2
- 239000003814 drug Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 238000009854 hydrometallurgy Methods 0.000 description 2
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 229910001427 strontium ion Inorganic materials 0.000 description 2
- UBXAKNTVXQMEAG-UHFFFAOYSA-L strontium sulfate Chemical compound [Sr+2].[O-]S([O-])(=O)=O UBXAKNTVXQMEAG-UHFFFAOYSA-L 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- SIIBQDDWAZKVLU-UHFFFAOYSA-J [Sr++].[Sr++].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O Chemical compound [Sr++].[Sr++].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O SIIBQDDWAZKVLU-UHFFFAOYSA-J 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 239000003792 electrolyte Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000005496 eutectics Effects 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- PIJPYDMVFNTHIP-UHFFFAOYSA-L lead sulfate Chemical compound [PbH4+2].[O-]S([O-])(=O)=O PIJPYDMVFNTHIP-UHFFFAOYSA-L 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- 238000003801 milling Methods 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
- 235000006408 oxalic acid Nutrition 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 230000005180 public health Effects 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 235000012239 silicon dioxide Nutrition 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 150000003751 zinc Chemical class 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- 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
- C22B26/00—Obtaining alkali, alkaline earth metals or magnesium
- C22B26/20—Obtaining alkaline earth metals or magnesium
-
- 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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- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
本发明公开了一种从锌阳极泥中分离回收锶的方法,该方法是将含锌阳极泥进行湿法球磨后,过滤,得到滤饼I;然后将所述滤饼I与碳酸盐溶液进行锶转化反应后,过滤,得到滤饼II;再将所述滤饼II采用稀酸低温浸出,得到含锶浸出液;所述含锶浸出液通过氢氧化钠溶液净化除杂,得到含锶净化液;向所述含锶净化液加入碳酸盐溶液进行沉淀反应,即得碳酸锶。该方法对阳极泥中锶回收率高达90%~99%,纯度达到94%~98%,同时药剂浓度和用量大大降低,对环境友好,工艺流程简单,且对设备要求低,有利于大规模推广应用。The invention discloses a method for separating and recovering strontium from zinc anode slime. The method is to carry out wet ball milling on the zinc-containing anode slime, and then filter to obtain filter cake I; and then mix the filter cake I with carbonate solution After carrying out the strontium conversion reaction, filter to obtain filter cake II; then leaching the filter cake II with dilute acid at low temperature to obtain strontium-containing leachate; the strontium-containing leachate is purified and removed by sodium hydroxide solution to obtain strontium-containing purified liquid ; Adding a carbonate solution to the strontium-containing purification solution for precipitation reaction to obtain strontium carbonate. The recovery rate of strontium in the anode slime is as high as 90%-99%, and the purity reaches 94%-98%. At the same time, the concentration and dosage of chemicals are greatly reduced. Promote apps.
Description
技术领域technical field
本发明涉及一种锌阳极泥的处理方法,特别涉及一种从锌阳极泥中分离回收锶的方法,属于化工技术领域。The invention relates to a method for treating zinc anode slime, in particular to a method for separating and recovering strontium from zinc anode slime, which belongs to the technical field of chemical industry.
背景技术Background technique
锶是一种具有独特物理和化学性能的金属,可广泛应用于电子、化工、冶金、焰火、军事、轻工、医药和光学等各个领域。中国的锶资源丰富,约占全球锶储量的四分之一。冶金工业的快速发展产生了大量的含锶二次资源。锶渣是碳酸锶精炼过程中产生的副产品,我国累计锶渣达4500万吨,并且以每年500万吨的速度增长。因此,从含锶二次资源中回收锶对于环境要求和锶资源安全具有重要意义。Strontium is a metal with unique physical and chemical properties, which can be widely used in various fields such as electronics, chemical industry, metallurgy, fireworks, military, light industry, medicine and optics. China is rich in strontium resources, accounting for about a quarter of the global strontium reserves. The rapid development of the metallurgical industry has produced a large number of secondary resources containing strontium. Strontium slag is a by-product produced in the refining process of strontium carbonate. The accumulative strontium slag in my country has reached 45 million tons, and it is increasing at a rate of 5 million tons per year. Therefore, the recovery of strontium from strontium-containing secondary resources is of great significance for environmental requirements and the safety of strontium resources.
锌阳极泥产自于湿法炼锌系统的电积过程。在电积过程中,常常向电解槽中加入碳酸锶以提高阴极锌的质量。碳酸锶在电解液中首先转化为硫酸锶,然后与硫酸铅共沉淀。每生产1吨锌就会产生约40-50公斤阳极泥。阳极泥除含锶、铅外,还含有锰、锌、钙等多种有价金属。废阳极泥的堆积处理方式不可避免地带来了资源利用不充分、对公众健康和环境造成严重污染等严重问题。因此,加强从锌电解阳极泥中分离和回收锶,已成为湿法炼锌工业必须解决的问题。Zinc anode slime is produced in the electrowinning process of the hydrometallurgy system. In the electrowinning process, strontium carbonate is often added to the electrolytic cell to improve the quality of the cathode zinc. Strontium carbonate is first converted to strontium sulfate in the electrolyte, and then co-precipitated with lead sulfate. About 40-50 kg of anode slime is produced for every ton of zinc produced. In addition to strontium and lead, anode slime also contains manganese, zinc, calcium and other valuable metals. The accumulation and treatment of waste anode slime inevitably brings serious problems such as insufficient resource utilization, serious pollution to public health and the environment. Therefore, strengthening the separation and recovery of strontium from zinc electrolytic anode slime has become a problem that must be solved in the zinc hydrometallurgy industry.
发明内容Contents of the invention
针对现有技术存在的技术缺陷,本发明的目的是在于提供一种从锌阳极泥中分离回收锶的方法。该方法利用球磨机械活化锌阳极泥中的锶,实现(Pb,Sr)SO4共晶结构的分离,并利用碳酸盐使硫酸锶锶转化成易溶于低浓度酸的碳酸锶,实现锶与其他金属高效分离,再利用氢氧化钠除去钙等杂质,最后利用碳酸盐沉淀锶,获得高纯碳酸锶产品,该方法对锶回收率高,同时可降低处理药剂浓度和用量,对环境友好,工艺流程简单,且对设备要求低,有利于大规模推广应用。Aiming at the technical defects existing in the prior art, the object of the present invention is to provide a method for separating and recovering strontium from zinc anode slime. The method utilizes ball milling machinery to activate strontium in zinc anode slime to realize the separation of (Pb,Sr)SO 4 eutectic structure, and uses carbonate to transform strontium strontium sulfate into strontium carbonate which is easily soluble in low-concentration acid to realize strontium Efficiently separate from other metals, then use sodium hydroxide to remove impurities such as calcium, and finally use carbonate to precipitate strontium to obtain high-purity strontium carbonate products. Friendly, simple process, and low requirements for equipment, which is conducive to large-scale promotion and application.
为了实现上述技术目的,本发明提供了一种从锌阳极泥中分离回收锶的方法,该方法是将含锌阳极泥进行湿法球磨后,过滤,得到滤饼I;将所述滤饼I与碳酸盐溶液进行锶转化反应后,过滤,得到滤饼II;将所述滤饼II采用稀酸低温浸出,得到含锶浸出液;将所述含锶浸出液通过氢氧化钠溶液净化除杂,得到含锶净化液;向所述含锶净化液中加入碳酸盐溶液进行沉淀反应,即得碳酸锶。In order to achieve the above technical purpose, the present invention provides a method for separating and recovering strontium from zinc anode slime, the method is to filter the zinc-containing anode slime after wet ball milling to obtain filter cake I; After carrying out the strontium conversion reaction with the carbonate solution, filter to obtain filter cake II; leaching the filter cake II with dilute acid at low temperature to obtain strontium-containing leaching solution; purifying the strontium-containing leaching solution through sodium hydroxide solution to remove impurities, A strontium-containing purification solution is obtained; a carbonate solution is added to the strontium-containing purification solution to carry out a precipitation reaction to obtain strontium carbonate.
本发明中锌阳极泥为湿法炼锌系统中电积过程中产生的含锶的阳极泥,其中锶含量为2~6wt%。The zinc anode slime in the present invention is the strontium-containing anode slime produced in the electrowinning process in the wet zinc smelting system, wherein the strontium content is 2-6 wt%.
本发明对锌阳极泥进行湿法球磨使其活化,然后添加碳酸盐溶液与活化的锌阳极泥进行化学反应使得其中的锶转化成易于在低浓度酸液中浸出的碳酸锶(SrCO3),从而结合低浓度酸液及低温浸出,在该条件下能够保证碳酸锶高效浸出,只包含少量钙等杂质,而锰、二氧化硅、铅等富集在渣相中,从而可以实现锶的富集分离。In the present invention, the zinc anode slime is activated by wet ball milling, and then a carbonate solution is added to chemically react with the activated zinc anode slime so that the strontium therein is converted into strontium carbonate (SrCO 3 ) which is easy to be leached in low-concentration acid solution , so as to combine low-concentration acid solution and low-temperature leaching, under this condition, the efficient leaching of strontium carbonate can be guaranteed, and only a small amount of impurities such as calcium are contained, while manganese, silicon dioxide, lead, etc. are enriched in the slag phase, so that strontium can be realized. Enrichment separation.
作为一个优选的方案,所述湿法球磨的条件为:转速为100~300r/min,固液比为1g:0.5~1.5ml,时间为0.5~1.5h。进一步优选的转速为150~250r/min。进一步优选的固液比为1g:0.9~1.1ml。进一步优选的时间为0.9~1.1h。As a preferred scheme, the conditions of the wet ball milling are as follows: the rotational speed is 100-300 r/min, the solid-liquid ratio is 1 g:0.5-1.5 ml, and the time is 0.5-1.5 h. A more preferred rotational speed is 150 to 250 r/min. A more preferable solid-to-liquid ratio is 1 g:0.9 to 1.1 ml. A further preferred time is 0.9 to 1.1 h.
在该球磨活化过程中,需控制合适的液固比以及球磨转速等条件,其中,液固比过高,将导致物料过于分散,使物料与球的接触不充分,降低湿式球磨效果,从而降低浸出效果;而液固比过低,将导致物料流动性较差,也会使物料与球的接触不充分,降低湿式球磨效果,从而降低浸出效果。同时,通过控制适当的球磨转速才有利于通过机械能实现锌阳极泥表面活化。During the ball milling activation process, it is necessary to control the appropriate liquid-solid ratio and ball milling speed and other conditions. Among them, if the liquid-solid ratio is too high, the material will be too dispersed, the contact between the material and the ball will be insufficient, and the effect of wet ball milling will be reduced. The leaching effect; if the liquid-solid ratio is too low, the fluidity of the material will be poor, and the contact between the material and the ball will be insufficient, which will reduce the effect of wet ball milling, thereby reducing the leaching effect. At the same time, the surface activation of zinc anode slime can be realized through mechanical energy by controlling the appropriate ball milling speed.
作为一个优选的方案,所述碳酸盐为碳酸钠、碳酸氢钠、碳酸铵、碳酸氢铵中至少一种。As a preferred solution, the carbonate is at least one of sodium carbonate, sodium bicarbonate, ammonium carbonate, and ammonium bicarbonate.
作为一个优选的方案,所述锶转化反应的条件为:滤饼I与碳酸盐溶液的固液比为1g:3~4mL,碳酸盐溶液的浓度为0.2~0.4mol/L;温度为85~95℃,时间为10~20min。进一步优选的碳酸盐溶液的浓度为0.25~0.33mol/L。在锶转化反应过程中,液固比过小,会使得混合物料的流动性不好,影响回收;液固比过大,会造成资源浪费,提升成本。同时,碳酸盐溶液浓度过小,会使得原料无法充分反应,导致锶的转化效率低;碳酸盐溶液浓度过大,会使得药剂的消耗增大,且无法取得对应的收益,影响经济效益。在锶转化反应过程中,温度越高,锶的转化效率越高,当温度为85~95℃时,锶的转化效率最佳。温度过高,会增加燃料成本,提升成本,降低经济效益;而温度过低,不仅会降低反应速率,同时也会降低锶的回收效果。As a preferred scheme, the conditions of the strontium conversion reaction are: the solid-to-liquid ratio of the filter cake I and the carbonate solution is 1g: 3-4mL, the concentration of the carbonate solution is 0.2-0.4mol/L; the temperature is 85~95℃, the time is 10~20min. A further preferred concentration of the carbonate solution is 0.25-0.33 mol/L. In the process of strontium conversion reaction, if the liquid-solid ratio is too small, the fluidity of the mixed material will be poor, which will affect the recovery; if the liquid-solid ratio is too large, it will cause waste of resources and increase costs. At the same time, if the concentration of carbonate solution is too small, the raw materials will not be able to fully react, resulting in low conversion efficiency of strontium; if the concentration of carbonate solution is too high, the consumption of chemicals will increase, and corresponding benefits cannot be obtained, which will affect economic benefits . During the conversion reaction process of strontium, the higher the temperature is, the higher the conversion efficiency of strontium is, and the conversion efficiency of strontium is the best when the temperature is 85-95°C. If the temperature is too high, it will increase fuel costs, increase costs, and reduce economic benefits; while if the temperature is too low, it will not only reduce the reaction rate, but also reduce the recovery effect of strontium.
作为一个优选的方案,所述稀酸低温浸出的条件为:以浓度为0.3~0.4mol/L的稀酸溶液作为浸出剂,所述滤饼II与稀酸溶液的固液比为1g:3~4mL,温度为20~40℃,时间为5~10min。在该稀酸浸出反应过程中,需控制稀酸浓度、固液比、反应温度在合适的范围有利于提高浸出效率。如果液固比过小,会使得混合物料的流动性不好,影响回收;液固比过大,会造成水资源浪费,提升成本。稀酸溶液浓度过小,原料无法充分反应,浸出效率降低;稀酸溶液浓度过大,会使得药剂的消耗增大,无法取得对应的收益,而且对设备的要求更高,影响经济效益。本发明稀酸浸出反应过程中,当温度为30℃时,锶的浸出达到最佳效果。温度过高,锶的浸出效率降低,影响锶的回收效果,还会增加酸的消耗量和燃料成本,提高生产成本;而温度过低,则会降低反应速率,影响锶的浸出效果。As a preferred solution, the conditions for the dilute acid low-temperature leaching are as follows: a dilute acid solution with a concentration of 0.3-0.4 mol/L is used as the leaching agent, and the solid-to-liquid ratio of the filter cake II to the dilute acid solution is 1g:3 ~4mL, the temperature is 20~40℃, and the time is 5~10min. During the dilute acid leaching reaction process, it is necessary to control the dilute acid concentration, solid-to-liquid ratio, and reaction temperature in an appropriate range to improve leaching efficiency. If the liquid-solid ratio is too small, the fluidity of the mixed material will be poor, affecting recycling; if the liquid-solid ratio is too large, water resources will be wasted and costs will increase. If the concentration of the dilute acid solution is too small, the raw materials cannot fully react, and the leaching efficiency will decrease; if the concentration of the dilute acid solution is too high, the consumption of chemicals will increase, and corresponding benefits cannot be obtained, and the requirements for equipment are higher, which affects economic benefits. In the dilute acid leaching reaction process of the present invention, when the temperature is 30 DEG C, the leaching of strontium reaches the best effect. If the temperature is too high, the leaching efficiency of strontium will decrease, which will affect the recovery effect of strontium, and will also increase the consumption of acid and fuel costs, and increase the production cost; while the temperature will be too low, the reaction rate will be reduced, and the leaching effect of strontium will be affected.
作为一个优选的方案,所述稀酸溶液为稀盐酸。本发明采用的稀盐酸不仅酸性较强,浸出效果好,而且废液污染较小,利于环保。相比于盐酸,草酸等弱酸的酸性较弱,浸出效果相对较差,而硝酸浸出会产生大量的含氮废液,容易造成水体富营养化,需要进行脱氮处理,提高生产成本。As a preferred solution, the dilute acid solution is dilute hydrochloric acid. The dilute hydrochloric acid adopted in the invention not only has strong acidity and good leaching effect, but also has less waste liquid pollution and is beneficial to environmental protection. Compared with hydrochloric acid, oxalic acid and other weak acids have weaker acidity, the leaching effect is relatively poor, while nitric acid leaching will produce a large amount of nitrogen-containing waste liquid, which is likely to cause eutrophication of the water body, and denitrification treatment is required to increase production costs.
作为一个优选的方案,所述净化过程为:采用浓度为8~12mol/L氢氧化钠溶液将含锶浸出液的pH值调节至12~13,过滤。最优选的pH值调节范围为12.5~12.7。As a preferred scheme, the purification process is as follows: adjusting the pH value of the leach solution containing strontium to 12-13 by using a sodium hydroxide solution with a concentration of 8-12 mol/L, and then filtering. The most preferred pH adjustment range is 12.5-12.7.
作为一个优选的方案,当稀酸低温浸出过程中的固液比为1g:3mL时,所述净化过程中采用氢氧化钠溶液将浸出液的pH值调节至12.5;当稀酸低温浸出过程中的固液比为1g:4mL时,所述净化过程中采用氢氧化钠溶液将浸出液的pH值调节至12.7。通过氢氧化钠溶液调节含锶浸出液的pH在12.5~12.7时,可使浸出液中部分金属离子杂质沉淀,从而提高锶回收纯度。在该净化除杂过程中,控制氢氧化钠溶液的浓度为10mol/L有利于提高净化效率。As a preferred scheme, when the solid-to-liquid ratio in the dilute acid low-temperature leaching process is 1g: 3mL, sodium hydroxide solution is used in the purification process to adjust the pH value of the leachate to 12.5; when the dilute acid low-temperature leaching process When the solid-to-liquid ratio was 1g:4mL, sodium hydroxide solution was used to adjust the pH value of the leachate to 12.7 during the purification process. When the pH of the strontium-containing leaching solution is adjusted to 12.5-12.7 by the sodium hydroxide solution, part of the metal ion impurities in the leaching solution can be precipitated, thereby improving the recovery purity of strontium. In the purification and impurity removal process, controlling the concentration of the sodium hydroxide solution to 10 mol/L is beneficial to improve the purification efficiency.
作为一个优选的方案,所述沉淀反应条件为:碳酸盐溶液中碳酸根离子与含锶净化液中锶离子的摩尔比为1.05~1.1:1。所述温度为20~40℃,时间为5~10min。锶沉淀反应过程中,控制碳酸盐溶液中碳酸根离子与净化液中锶离子的摩尔比为1.05~1.1:1可获得较好的锶回收效果。As a preferred solution, the precipitation reaction condition is: the molar ratio of carbonate ions in the carbonate solution to strontium ions in the strontium-containing purification solution is 1.05˜1.1:1. The temperature is 20-40° C., and the time is 5-10 minutes. During the strontium precipitation reaction, controlling the molar ratio of carbonate ions in the carbonate solution to strontium ions in the purification solution to be 1.05-1.1:1 can obtain a better strontium recovery effect.
作为一个优选的方案,所述碳酸盐溶液为饱和溶液。进一步优选的碳酸盐溶液为碳酸钠溶液。As a preferred solution, the carbonate solution is a saturated solution. A further preferred carbonate solution is sodium carbonate solution.
相对现有技术,本发明技术方案带来的有益效果在于:Compared with the prior art, the beneficial effects brought by the technical solution of the present invention are:
(1)采用机械化学球磨、低酸低温浸出及沉淀反应等相结合手段,实现了锌阳极泥中锶的高效转化及与金属杂质的高效分离,获得的锶回收率达到90%~99%,锶产品的纯度可以达到94%~98%。(1) The combination of mechanochemical ball milling, low-acid low-temperature leaching and precipitation reaction has realized the efficient conversion of strontium in zinc anode slime and the efficient separation of metal impurities, and the recovery rate of strontium obtained has reached 90% to 99%. The purity of strontium products can reach 94% to 98%.
(2)通过采用机械化学球磨技术使得低锌阳极泥中的锶高效地转化成易溶于低浓度酸液的碳酸锶(SrCO3),从而在低浓度酸液下实现锶高效浸出,实现锶与杂质的分离。(2) The strontium in the low-zinc anode slime is efficiently converted into strontium carbonate (SrCO 3 ) which is easily soluble in low-concentration acid solution by using mechanochemical ball milling technology, so as to achieve efficient leaching of strontium in low-concentration acid solution and realize strontium Separation from impurities.
(3)方法简单,大大降低药剂浓度及用量,对环境友好,对设备要求低,有利于大规模推广应用。(3) The method is simple, greatly reduces the concentration and dosage of the medicament, is environmentally friendly, has low requirements on equipment, and is conducive to large-scale popularization and application.
具体实施方式detailed description
下面结合具体实施例对本发明作进一步解释和说明。这些实施例仅为了更好的理解本发明,而不是限制本发明所保护的范围。The present invention will be further explained and illustrated below in conjunction with specific embodiments. These examples are only for better understanding of the present invention, rather than limiting the protection scope of the present invention.
实施例1Example 1
本实施例提供一种从锌阳极泥中分离回收锶的方法,其具体步骤如下:This embodiment provides a method for separating and recovering strontium from zinc anode slime, and its specific steps are as follows:
(1)取含锶的锌阳极泥100g(成分如表1所示),放入容积为1L的球磨罐中进行机械化学球磨,控制固液比为1g:1ml,球磨转速为200r/min,球磨时间为1h。(1) Take 100g of strontium-containing zinc anode slime (the composition is shown in Table 1), put it into a ball mill tank with a volume of 1L for mechanochemical ball milling, control the solid-liquid ratio to 1g:1ml, and the ball milling speed to 200r/min, The ball milling time is 1h.
(2)将机械化学球磨产物与0.25mol/L的碳酸钠溶液混合,控制固液比为1g:4ml,浸出温度为95℃,时间20min,过滤,得到含碳酸锶的滤饼。(2) Mix the mechanochemical ball milled product with 0.25mol/L sodium carbonate solution, control the solid-liquid ratio to 1g:4ml, leaching at 95°C for 20min, and filter to obtain a filter cake containing strontium carbonate.
(3)将含碳酸锶的滤饼与0.3mol/L盐酸混合,控制固液比为1g:4ml,浸出温度为30℃,时间10min,对浸出产物过滤,得到含锶滤液。(3) Mix the filter cake containing strontium carbonate with 0.3mol/L hydrochloric acid, control the solid-liquid ratio to 1g:4ml, leach at a temperature of 30°C for 10min, and filter the leached product to obtain a strontium-containing filtrate.
(4)向含锶滤液加入10mol/L的氢氧化钠溶液调节pH值为12.7,过滤,得到含锶净化液。(4) Add 10 mol/L sodium hydroxide solution to the strontium-containing filtrate to adjust the pH value to 12.7, and filter to obtain a strontium-containing purified solution.
(5)将含锶净化液与饱和碳酸钠溶液混合进行沉淀反应,控制碳酸根离子与净化液中锶的摩尔比为1.1:1,反应温度为30℃,时间为10分钟,过滤反应产物,得到固体,烘干,即为碳酸锶。(5) Mix the strontium-containing purification solution with saturated sodium carbonate solution for precipitation reaction, control the molar ratio of carbonate ions to strontium in the purification solution to be 1.1:1, the reaction temperature is 30°C, and the time is 10 minutes, and the reaction product is filtered. Obtain solid, drying, that is strontium carbonate.
经计算,在本实施条件下,锶回收率为98.29%,产品纯度为97.61%。After calculation, under the conditions of this implementation, the recovery rate of strontium is 98.29%, and the product purity is 97.61%.
表1某锌阳极泥成分,wt%Table 1 Composition of certain zinc anode slime, wt%
实施例2Example 2
本实施例提供另一种从锌阳极泥中分离回收锶的方法,其具体步骤如下:This embodiment provides another method for separating and recovering strontium from zinc anode slime, and its specific steps are as follows:
(1)取含锶的锌阳极泥100g(成分如表1所示),放入容积为1L的球磨罐中进行机械化学球磨,控制固液比为1g:0.9ml,球磨转速为200r/min,球磨时间为1h。(1) Take 100g of strontium-containing zinc anode slime (the composition is shown in Table 1), put it into a ball mill tank with a volume of 1L for mechanochemical ball milling, control the solid-liquid ratio to 1g:0.9ml, and the ball milling speed to 200r/min , the milling time is 1h.
(2)将机械化学球磨产物与0.33mol/L的碳酸钠溶液混合,控制固液比为1g:3ml,浸出温度为85℃,时间10min,过滤,得到含碳酸锶的滤饼。(2) Mix the mechanochemical ball milled product with 0.33mol/L sodium carbonate solution, control the solid-liquid ratio to 1g:3ml, leaching at 85°C for 10min, and filter to obtain a filter cake containing strontium carbonate.
(3)将含碳酸锶的滤饼与0.4mol/L盐酸混合,控制固液比为1g:3ml,浸出温度为30℃,时间5min,对浸出产物过滤,得到含锶滤液。(3) Mix the filter cake containing strontium carbonate with 0.4mol/L hydrochloric acid, control the solid-liquid ratio to 1g:3ml, leach at 30°C for 5min, and filter the leached product to obtain strontium-containing filtrate.
(4)向含锶滤液加入10mol/L的氢氧化钠溶液调节pH值为12.5,过滤,得到净化液。(4) Add 10 mol/L sodium hydroxide solution to the strontium-containing filtrate to adjust the pH value to 12.5, and filter to obtain a purified solution.
(5)将净化液与饱和碳酸钠溶液混合进行沉淀反应,控制碳酸根离子与净化液中锶的摩尔比为1.05:1,反应温度为30℃,时间为5分钟,过滤反应产物,得到固体,烘干,即为碳酸锶。(5) Mix the purification solution with saturated sodium carbonate solution for precipitation reaction, control the molar ratio of carbonate ions and strontium in the purification solution to 1.05:1, the reaction temperature is 30°C, and the time is 5 minutes, and the reaction product is filtered to obtain a solid , drying, that is, strontium carbonate.
经计算,在本实施条件下,锶回收率为92.47%,产品纯度为94.89%。After calculation, under the conditions of this implementation, the recovery rate of strontium is 92.47%, and the product purity is 94.89%.
实施例3Example 3
本实施例提供第三种从锌阳极泥中分离回收锶的方法,其具体步骤如下:This embodiment provides the third method for separating and recovering strontium from zinc anode slime, and its specific steps are as follows:
(1)取含锶的锌阳极泥100g(成分如表1所示),放入容积为1L的球磨罐中进行机械化学球磨,控制固液比为1g:1.1ml,球磨转速为200r/min,球磨时间为1.1h。(1) Take 100g of strontium-containing zinc anode slime (the composition is shown in Table 1), put it into a ball mill tank with a volume of 1L for mechanochemical ball milling, control the solid-liquid ratio to 1g:1.1ml, and the ball milling speed to 200r/min , The ball milling time is 1.1h.
(2)将机械化学球磨产物与0.25mol/L的碳酸钠溶液混合,固液比为1g:4ml,浸出温度为90℃,时间10min,过滤,得到含碳酸锶的滤饼。(2) Mix the mechanochemical ball milled product with 0.25mol/L sodium carbonate solution, the solid-to-liquid ratio is 1g:4ml, the leaching temperature is 90°C, and the time is 10min, and filter to obtain a filter cake containing strontium carbonate.
(3)将含碳酸锶的滤饼与0.3mol/L盐酸混合,控制固液比为1g:4ml,浸出温度为30℃,时间10min,对浸出产物过滤,得到含锶滤液。(3) Mix the filter cake containing strontium carbonate with 0.3mol/L hydrochloric acid, control the solid-liquid ratio to 1g:4ml, leach at a temperature of 30°C for 10min, and filter the leached product to obtain a strontium-containing filtrate.
(4)向含锶滤液加入10mol/L的氢氧化钠溶液调节pH值为12.7,过滤,得到净化液。(4) Add 10 mol/L sodium hydroxide solution to the strontium-containing filtrate to adjust the pH value to 12.7, and filter to obtain a purified solution.
(5)将净化液与饱和碳酸钠溶液混合进行沉淀反应,控制碳酸根离子与净化液中锶的摩尔比为1.1:1,反应温度为30℃,时间为10分钟,过滤反应产物,得到固体,烘干,即为碳酸锶。(5) Mix the purification solution with saturated sodium carbonate solution for precipitation reaction, control the molar ratio of carbonate ions and strontium in the purification solution to 1.1:1, the reaction temperature is 30°C, the time is 10 minutes, and the reaction product is filtered to obtain a solid , drying, that is, strontium carbonate.
经计算,在本实施条件下,锶回收率为90.36%,产品纯度为95.1%。After calculation, under the conditions of this implementation, the recovery rate of strontium is 90.36%, and the product purity is 95.1%.
实施例4Example 4
本实施例提供第三种从锌阳极泥中分离回收锶的方法,其具体步骤如下:This embodiment provides the third method for separating and recovering strontium from zinc anode slime, and its specific steps are as follows:
(1)取含锶的锌阳极泥100g(成分如表1所示),放入容积为1L的球磨罐中进行机械化学球磨,控制固液比为1g:0.9ml,球磨转速为200r/min,球磨时间为0.9h。(1) Take 100g of strontium-containing zinc anode slime (the composition is shown in Table 1), put it into a ball mill tank with a volume of 1L for mechanochemical ball milling, control the solid-liquid ratio to 1g:0.9ml, and the ball milling speed to 200r/min , The ball milling time is 0.9h.
(2)将机械化学球磨产物与0.33mol/L的碳酸钠溶液混合,控制固液比为1g:3ml,浸出温度为85℃,时间10min,过滤,得到含碳酸锶的滤饼。(2) Mix the mechanochemical ball milled product with 0.33mol/L sodium carbonate solution, control the solid-liquid ratio to 1g:3ml, leaching at 85°C for 10min, and filter to obtain a filter cake containing strontium carbonate.
(3)将含碳酸锶的滤饼与0.4mol/L盐酸混合,控制固液比为1g:3ml,浸出温度为30℃,时间5min,对浸出产物过滤,得到含锶滤液。(3) Mix the filter cake containing strontium carbonate with 0.4mol/L hydrochloric acid, control the solid-liquid ratio to 1g:3ml, leach at 30°C for 5min, and filter the leached product to obtain strontium-containing filtrate.
(4)向含锶滤液加入10mol/L的氢氧化钠溶液调节pH值为12.5,过滤,得到净化液。(4) Add 10 mol/L sodium hydroxide solution to the strontium-containing filtrate to adjust the pH value to 12.5, and filter to obtain a purified solution.
(5)将净化液与饱和碳酸钠溶液混合进行沉淀反应,控制碳酸根离子与净化液中锶的摩尔比为1.05:1,反应温度为30℃,时间为5分钟,过滤反应产物,得到固体,烘干,即为碳酸锶。(5) Mix the purification solution with saturated sodium carbonate solution for precipitation reaction, control the molar ratio of carbonate ions and strontium in the purification solution to 1.05:1, the reaction temperature is 30°C, and the time is 5 minutes, and the reaction product is filtered to obtain a solid , drying, that is, strontium carbonate.
经计算,在本实施条件下,锶回收率为95.7%,产品纯度为96.35%。After calculation, under the present implementation conditions, the strontium recovery rate is 95.7%, and the product purity is 96.35%.
对比例1Comparative example 1
在实施例1的基础上,将球磨过程中的固液比调整为1g:3ml,球磨时间调整为0.5h,其他条件保持不变。On the basis of Example 1, the solid-to-liquid ratio in the ball milling process was adjusted to 1g:3ml, the ball milling time was adjusted to 0.5h, and other conditions remained unchanged.
经计算,在该对比例条件下,锶回收率仅为34.83%。It is calculated that under the conditions of the comparative example, the recovery rate of strontium is only 34.83%.
对比例2Comparative example 2
在实施例1的基础上,将步骤(2)碳酸钠转化反应中反应温度调整为50℃,反应时间调整为5min,其他条件保持不变。On the basis of Example 1, the reaction temperature in step (2) sodium carbonate conversion reaction was adjusted to 50° C., the reaction time was adjusted to 5 min, and other conditions remained unchanged.
经计算,在该对比例条件下,锶回收率仅为47.32%。It is calculated that under the conditions of the comparative example, the recovery rate of strontium is only 47.32%.
对比例3Comparative example 3
在实施例1的基础上,将步骤(3)酸浸出反应中的浸出温度调整为90℃,其他条件保持不变。On the basis of Example 1, the leaching temperature in the acid leaching reaction in step (3) was adjusted to 90° C., and other conditions remained unchanged.
经计算,在该对比例条件下,锶回收率仅为57.58%。It is calculated that under the conditions of the comparative example, the recovery rate of strontium is only 57.58%.
对比例4Comparative example 4
在实施例1的基础上,将步骤(5)沉淀反应中的碳酸根离子与浸出液中锶的摩尔比调整为1:1,其他条件保持不变。On the basis of Example 1, the molar ratio of carbonate ions in the precipitation reaction in step (5) to strontium in the leaching solution was adjusted to 1:1, and other conditions remained unchanged.
经计算,在该对比例条件下,锶回收率为80.28%,纯度为95.34%。It is calculated that under the conditions of the comparative example, the recovery rate of strontium is 80.28%, and the purity is 95.34%.
综上所述,通过对比实施例分析,对于锌阳极泥,机械化学球磨和碳酸钠转化-低浓度盐酸低温浸出可以明显提高回收效率,且此方法工艺流程简单,对设备要求低,适合工业化大规模生产。In summary, through the analysis of comparative examples, for zinc anode slime, mechanochemical ball milling and sodium carbonate conversion-low-concentration hydrochloric acid low-temperature leaching can significantly improve recovery efficiency, and this method has a simple process flow and low equipment requirements, and is suitable for large-scale industrialization. mass production.
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