WO2023092480A1 - 一种从高冰镍中提取硫酸镍的方法 - Google Patents

一种从高冰镍中提取硫酸镍的方法 Download PDF

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WO2023092480A1
WO2023092480A1 PCT/CN2021/133610 CN2021133610W WO2023092480A1 WO 2023092480 A1 WO2023092480 A1 WO 2023092480A1 CN 2021133610 W CN2021133610 W CN 2021133610W WO 2023092480 A1 WO2023092480 A1 WO 2023092480A1
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nickel
leaching
slurry
liquid
sulfate
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PCT/CN2021/133610
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English (en)
French (fr)
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李萍
赵志明
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深圳市坤鹏冶金工程技术有限公司
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Priority to PCT/CN2021/133610 priority Critical patent/WO2023092480A1/zh
Priority to CN202180081614.5A priority patent/CN116568831A/zh
Publication of WO2023092480A1 publication Critical patent/WO2023092480A1/zh

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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
    • C22B11/00Obtaining noble metals
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • 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
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Definitions

  • the invention belongs to the technical field of non-ferrous metal hydrometallurgy, and in particular relates to a method for extracting nickel sulfate from high nickel matte.
  • the traditional nickel sulfate production process is mainly to produce high nickel matte through pyrometallurgy of nickel sulfide ore, and then use wet process to produce nickel sulfate.
  • the reserves of nickel sulfide ore have dropped sharply, mining difficulty has increased, and nickel grade has decreased.
  • the cost of mining has risen, and the international nickel industry has shifted from the development and utilization of nickel sulfide ore to nickel laterite ore.
  • the production of nickel sulfate from nickel laterite mainly uses the pressurized acid leaching process to produce nickel cobalt hydroxide, and then produces nickel sulfate solution after acid dissolution, extraction and impurity removal. Higher, lower production capacity, unable to meet the market demand for nickel sulfate.
  • the invention discloses a method for producing nickel sulfate obtained from high nickel matte obtained from nickel laterite ore, which changes the current situation of low production capacity of nickel sulfate produced from nickel laterite ore, so as to meet the rapidly growing demand of the nickel sulfate market in the battery industry.
  • the invention provides a method for extracting nickel sulfate from high nickel matte.
  • the invention provides a method for extracting nickel sulfate from high nickel matte, the method comprising:
  • the purified and impurity-removed slag is slurried by using the solution before nickel immersion at atmospheric pressure; then, the purified and impurity-removed slurry after slurry is sequentially subjected to atmospheric nickel immersion and pressurized nickel immersion; finally, solid-liquid separation is obtained. Pressure leaching liquid and pressure leaching residue;
  • the atmospheric pressure nickel immersion pre-liquid is obtained by mixing the pressure leaching liquid, water, sulfuric acid and copper sulfate of the back-end process, wherein the Cu concentration in the atmospheric pressure nickel immersion pre-liquid is 1-20g /L.
  • the significance of the Cu 2+ concentration being 1-20g/L is that copper can accelerate the leaching reaction and prevent hydrogen sulfide from coming out of the pulp from causing damage to equipment and human body.
  • the concentration of Cu 2+ in the solution before nickel immersion at atmospheric pressure can be 1g/L, 20g/L, or any concentration in the range of 1-20g/L, and the specific concentration is determined according to the actual situation.
  • the process of purifying and removing impurities includes: adding compressed air or oxygen-enriched air to the slurried high-nickel matte slurry, and controlling the pH of the reaction end point of purifying and removing impurities to be 4.0-6.5.
  • the purpose of adding the oxidizing agent is to oxidize the ferrous iron in the high nickel matte slurry after slurrying, and prepare for the heavy iron in the purification process.
  • the purpose of controlling the pH of the reaction end point of purification and removal of impurities to be 4.0 to 6.5 is to completely precipitate iron and copper as much as possible.
  • Controlling the pH of the reaction end point of purification and removal of impurities to be 4.0 to 6.5 means that in a specific embodiment, the pH of the reaction end point of purification and removal of impurities can be 4.0, 6.5, or any value within the range of 4.0 to 6.5.
  • the pH is determined according to the actual situation, and it may also be a dynamic pH value, but the dynamic pH is also in the range of 4.0 to 6.5.
  • the reaction temperature is controlled at 60-90° C.
  • the ventilation rate is 500-2500 NM 3 /t material
  • the reaction time is 3 h-8 h.
  • the reaction temperature may be 60°C, 90°C, or any temperature value within the range of 60-90°C.
  • the ventilation rate can be 500 NM 3 /t material, 2500 NM 3 /t material, or any ventilation rate value in the range of 500-2500 NM 3 /t material.
  • the reaction time may be 3 hours, 8 hours, or any time point in 3-8 hours according to the actual situation.
  • adding an oxidizing agent to the slurried high-nickel matte slurry specifically includes: feeding compressed air or oxygen-enriched air into the slurried high-nickel matte slurry.
  • the process of nickel leaching at atmospheric pressure includes: passing compressed air or oxygen-enriched air into the pulped slurry for purifying and removing impurities, and controlling the pH value at the end of the reaction by controlling the amount of sulfuric acid added 0.5 to 3.5, the purpose of controlling the reaction pH at this time is to provide suitable acidity for normal pressure nickel immersion and pressure immersion nickel, because pressure immersion nickel within this acidity can completely react the metal nickel and prevent Hydrogen gas is produced. At this time, a small part of the compressed air or oxygen-enriched air is involved in the reaction, and most of it is discharged from the reaction system.
  • Controlling the pH at the end of the reaction to be 0.5 to 3.5 by controlling the amount of sulfuric acid added means that in a specific embodiment, the pH at the end of the reaction can be controlled to be 0.5 by controlling the amount of sulfuric acid added, and the pH at the end of the reaction can be made to be 0.5. 3.5, and the pH value at the end of the reaction can also be any value within the range of 0.5 to 3.5.
  • the reaction temperature is controlled at 60-90° C.
  • the ventilation rate is 500-2500 NM 3 /t material
  • the time is 3-8 hours.
  • the pressure leaching process includes: adding an oxidant to the slurry after nickel leaching at atmospheric pressure, controlling the temperature at 130-220°C, the reaction time at 2h-8h, the oxygen partial pressure at 0.1-1.5 Mpa, and the pH at the end of the reaction
  • the value is 1.0 to 3.5.
  • the purpose of controlling the reaction temperature, reaction time, oxygen partial pressure and pH at the end of the reaction during the pressure leaching nickel process is to make the nickel leached as completely as possible, reduce the nickel content in the pressure leaching slag as much as possible, and avoid the waste of nickel.
  • the reaction temperature of pressure leaching may be 130°C, 220°C, or any temperature value within the range of 130-220°C.
  • the reaction time may be 2 hours, 8 hours, or any time point value between 2 hours and 8 hours.
  • the oxygen partial pressure can be 0.1 Mpa, can be 1.0 Mpa, can be 1.2 Mpa, can be 1.5 Mpa, can also be 0.1 ⁇ 1.5 Any value in the MPa range.
  • Oxygen partial pressure is lower than 0.1Mpa and can influence the leaching rate of nickel; And oxygen partial pressure is higher than 1.5 Mpa and can not bring the effective improvement of nickel leaching rate, but can have higher requirement to the equipment that is applied to the present invention, and then causes The cost of the whole process increases.
  • the pH value at the end of the reaction may be 1.0, 3.5, or any value within the range of 1.0-3.5.
  • adding the oxidizing agent to the pulp after nickel leaching at atmospheric pressure includes: passing oxygen into the pulp after nickel leaching at atmospheric pressure.
  • the slurry solid-liquid ratio is controlled to be 4-10:1, and the slurrying time is 0.5-2 hours.
  • the solid-to-liquid ratio can be 4:1, 10:1, or any ratio within the range of 4-10:1.
  • the purpose is to fully mix the high nickel matte with the liquid after pressure leaching.
  • the slurry solid-liquid ratio is controlled to be 4-10:1, and the slurrying time is 0.5-2 hours.
  • the solid-to-liquid ratio can be 4:1, 10:1, or any ratio within the range of 4 to 10:1. Mix well.
  • Nickel exists in two forms in high-matte nickel, one is metallic phase nickel, and the other is non-metallic phase nickel; wherein the content of non-metallic phase nickel is relatively large, and in the present invention, only partial The metal phase nickel and impurities are leached by replacement reaction, and a large amount of non-metallic phase nickel and the remaining part of the metal phase nickel exist in the purification and impurity removal slag; in order to realize the recovery of nickel in the purification and impurity removal slag, so in the present invention It is also necessary to continue to slurry the purified and impurity-removing slag, and then sequentially adopt the methods of atmospheric nickel leaching and pressure leaching to leach nickel into the liquid after pressure leaching, so as to realize the recovery of nickel in high nickel matte and avoid the waste liquid.
  • the leaching rate of nickel and cobalt can reach more than 98%; in the nickel and cobalt sulfate solution produced by purification and removal of impurities, Ni ⁇ 90g/L, Cu ⁇ 0.01g/L, Fe ⁇ 0.01g/L; the pressure leaching residue contains less than 1% nickel, while the iron content reaches more than 55%, so that the pressure leaching slag can be used as iron raw material for export, avoiding the generation of waste slag. At the same time, there is no waste gas generation in the whole preparation process.
  • Fig. 1 is a flow chart of a method for extracting nickel sulfate from high nickel matte provided by the present invention.
  • the present invention provides a kind of method extracting nickel sulfate from high nickel matte, and the method comprises:
  • the purpose is to fully mix the treated high-nickel matte with the pressure leaching solution; then, purify the high-nickel matte slurry after slurrying Impurity removal, solid-liquid separation, obtaining nickel-cobalt sulfate solution and purifying impurity-removing slag, at this time, the separation of nickel-cobalt and impurities is realized;
  • Slurry is carried out on the purification and removal of impurities by using the solution before atmospheric nickel immersion; then, the slurry of purification and removal of impurities after slurry is sequentially subjected to atmospheric pressure nickel immersion and pressure nickel immersion; finally, solid-liquid separation is carried out to obtain pressurized After leaching liquid and pressure leaching residue;
  • Atmospheric pressure nickel immersion pre-liquid is obtained by mixing the post-pressure leaching liquid, water, sulfuric acid and copper sulfate in the back-end process, and the concentration of Cu 2+ in the atmospheric pressure nickel immersion pre-liquid is 1 ⁇ 20g/L.
  • Nickel exists in two forms in high-matte nickel, one is metallic phase nickel, and the other is non-metallic phase nickel; wherein the content of non-metallic phase nickel is relatively large, and in the present invention, only partial Metallic nickel is leached by replacement reaction with impurities, and a large amount of non-metallic nickel and the rest of metallic nickel exist in the purification and impurity removal slag; in order to realize the recovery of non-metallic nickel, it is necessary to continue the process in the present invention.
  • This embodiment provides a method for extracting nickel sulfate from high-nickel matte, wherein high-nickel matte comes from nickel laterite ore, and its composition (%) is: Ni ⁇ 78, Fe ⁇ 1, Co ⁇ 1, S ⁇ 20.
  • the method for extracting nickel sulfate from above-mentioned high nickel matte specifically comprises the steps:
  • the pressurized leaching liquid produced by the back-end process of this embodiment is mixed with the material obtained by the above-mentioned ball mill for slurrying, wherein the slurrying solid-liquid ratio is 8:1, and the slurrying time is 1 hour to obtain a high nickel matte slurry;
  • Nickel-cobalt sulfate solution (g/L): Ni 96.38, Cu 0.006, Fe 0.003, Co 1.26.
  • This example provides a method for extracting nickel sulfate from high-nickel matte, wherein high-nickel matte comes from nickel laterite ore, and its composition (%) is: Ni ⁇ 75, Fe ⁇ 1, Co ⁇ 1, S ⁇ 22.
  • the method for extracting nickel sulfate from above-mentioned high nickel matte specifically comprises the steps:
  • the pressurized leaching liquid produced by the back-end process of this embodiment is mixed with the material obtained by the above ball mill for slurrying, wherein the slurrying solid-liquid ratio is 7:1, and the slurrying time is 1 hour to obtain a high nickel matte slurry;
  • Nickel-cobalt sulfate solution (g/L): Ni 101.65, Cu 0.0001, Fe 0.001, Co 1.48.

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Abstract

本发明公开了一种从高冰镍中提取硫酸镍的方法,该方法包括:采用后端工艺产出的加压浸出后液对处理后的高冰镍进行浆化;然后,对浆化后的高冰镍浆料进行净化除杂,固液分离,得到硫酸镍钴溶液和净化除杂渣;采用常压浸镍前液对所述净化除杂渣进行浆化;然后,对浆化后的净化除杂渣浆料依次进行常压浸镍和加压浸镍;最后,固液分离,得到加压浸出后液和加压浸出渣;所述常压浸镍前液是通过将后端工艺的加压浸出后液、硫酸和硫酸铜混合得到的,其中所述常压浸镍前液中的Cu 2+浓度为1~20g/L。通过本发明的方法能够实现无三废排出,镍钴浸出率达到98%以上,加压浸出渣能够作为铁原料外销。

Description

一种从高冰镍中提取硫酸镍的方法 技术领域
本发明属于有色金属湿法冶金技术领域,具体涉及一种从高冰镍中提取硫酸镍的方法。
背景技术
近年来,新能源汽车快速发展,汽车动力电池要求的能量密度不断提高,而目前市场成熟的正极只有三元材料可以满足,高镍是未来三元材料发展方向。因此,硫酸镍作为新能源电池材料需求旺盛,其产能、产量也将呈爆发式增长。
目前,传统的硫酸镍生产工艺主要是通过硫化镍矿火法冶炼生产高冰镍再采用湿法工艺生产硫酸镍,经过长期开采,硫化镍矿的保有储量急剧下降,开采难度加大,镍品位降低,开采成本升高,国际镍工业已从硫化镍矿向镍红土矿开发利用转变。镍红土矿生产硫酸镍主要是采用加压酸浸工艺生产氢氧化镍钴,再通过酸溶解、萃取除杂等工序后产出硫酸镍溶液,该工艺处理流程较长,且投资成本和运行成本较高,产能较低,无法满足硫酸镍市场需求。
随着镍红土矿火法冶炼高冰镍技术的逐渐成熟,镍红土矿冶炼高冰镍开始规模化生产,而镍红土矿产出的高冰镍物料与传统的硫化矿产出高冰镍存在不同的矿物特性,需要针对性的提出一种镍红土矿得到的高冰镍生产的硫酸镍的方法,改变现有镍红土矿生产硫酸镍产能低的现状,以满足电池行业硫酸镍市场快速增长的需求。
技术问题
为了解决目前从高冰镍中提取硫酸镍存在的产能低的问题,本发明提供一种从高冰镍中提取硫酸镍的方法。
技术解决方案
本发明提供了一种高冰镍中提取硫酸镍的方法,该方法包括:
采用后端工艺产出的加压浸出后液对处理后的高冰镍进行浆化;然后,对浆化后的高冰镍浆料进行净化除杂,固液分离,得到硫酸镍钴溶液和净化除杂渣;
采用常压浸镍前液对所述净化除杂渣进行浆化;然后,对浆化后的净化除杂渣浆料依次进行常压浸镍和加压浸镍;最后,固液分离,得到加压浸出后液和加压浸出渣;
所述常压浸镍前液是通过将后端工艺的加压浸出后液、水、硫酸和硫酸铜混合得到的,其中所述常压浸镍前液中的Cu 2+浓度为1~20g/L。
Cu 2+浓度为1~20g/L的意义是,铜可以加速浸出反应的进行,同时防止硫化氢从矿浆中冒出对设备和人体造成损伤。常压浸镍前液中的Cu 2+浓度可以为1g/L,可以为20g/L,也可以是1~20g/L中任意浓度,具体浓度根据实际情况决定。
进一步的,所述净化除杂的过程包括:向浆化后的高冰镍浆料中加入压缩空气或富氧空气,并控制净化除杂的反应终点pH为4.0~6.5。加入氧化剂的目的是为了氧化浆化后的高冰镍浆料中的二价铁,为净化工艺中的沉铁做准备。而控制净化除杂的反应终点pH为4.0~6.5的目的是为了尽量使铁和铜完全沉出。
控制净化除杂的反应终点pH为4.0~6.5的意思是在具体实施例中,净化除杂的反应终点pH可以为4.0,可以为6.5,也可以为4.0~6.5范围内的任意数值,具体的pH根据实际情况决定,也可能是一个动态的pH值,但是动态的pH也处于4.0~6.5范围内。
进一步的,所述净化除杂的过程中控制反应温度60~90℃,通风量500~2500NM 3/t物料,反应时间3 h~8h。在具体实施例中,反应温度可以是60℃,可以是90℃,也可以是60~90℃范围内的任意温度值。在具体实施例中,通风量可以是500 NM 3/t物料,可以是2500NM 3/t物料,也可以是500~2500NM 3/t物料中的任意一个通风量数值。在具体实施例中,根据实际情况反应时间可以是3h,可以是8h,也可以是3~8h中的任意时间点。
进一步的,向浆化后的高冰镍浆料中加入氧化剂具体包括:向浆化后的高冰镍浆料中通入压缩空气或富氧空气。
进一步的,所述常压浸镍的过程包括:将压缩空气或富氧空气通入到浆化后的净化除杂渣浆料中,并通过控制硫酸的加入量来控制反应终点的pH值为0.5~3.5,此时控制反应pH的目的是为常压浸镍和加压浸镍提供适合的酸度,因为在此酸度内进行加压浸镍能够使金属镍反应完全,防止加压时会有氢气产生。此时通入的压缩空气或富氧空气小部分参与反应,大部分又被排出反应体系。
通过控制硫酸的加入量来控制反应终点的pH值为0.5~3.5的意思是在具体实施例中,通过控制硫酸的加入量可以使反应终点的pH值为0.5,可以使反应终点的pH值为3.5,也可以使反应终点的pH值在0.5~3.5范围内的任意数值。
进一步的,所述常压浸镍的过程中还控制反应温度60~90℃,通风量500~2500NM 3/t物料,时间3~8h。
进一步的,所述加压浸出过程包括:将氧化剂加入到常压浸镍后矿浆中,控制温度为130~220℃,反应时间为2h~8h,氧分压为0.1~1.5 Mpa,反应终点pH值1.0~3.5。在加压浸镍过程中通过控制反应温度,反应时间,氧分压和反应终点pH的目的是为了使镍尽量完全浸出,尽量降低加压浸出渣中镍的含量,避免镍的浪费。
在具体实施例中,加压浸出的反应温度可以是130℃,可以是220℃,也可以是130~220℃范围内的任意温度值。在具体实施例中,反应时间可以为2h,可以为8h,也可以为2h~8h中的任意时间点值。在具体实施例中,氧分压可以为0.1 Mpa,可以为1.0 Mpa,可以为1.2 Mpa,可以为1.5 Mpa,还可以为0.1~1.5 Mpa范围中的任意值。氧分压低于0.1Mpa会影响镍的浸出率;而氧分压高于1.5 Mpa并不会带来镍浸出率的有效提高,但是会对应用于本发明的设备具有更高的要求,进而导致整个工艺过程的成本增加。在具体实施例中,反应终点pH值可以为1.0,可以为3.5,还可以为1.0~3.5范围中的任意值。
进一步的,将氧化剂加入到常压浸镍后矿浆中包括:将氧气通入到常压浸镍后矿浆中。
进一步的,采用后端工艺产出的加压浸出后液对处理后的高冰镍进行浆化的过程中,控制浆化固液比为4~10:1,浆化时间为0.5~2h。在具体实施例中,固液比可以为4:1,可以为10:1,也可以是4~10:1范围内的任意比值,其目的是使高冰镍与加压浸出后液充分混合。
进一步的,采用常压浸镍前液对所述净化除杂渣进行浆化的过程中,控制浆化固液比为4~10:1,浆化时间为0.5~2h。在具体实施例中,固液比可以为4:1,可以为10:1,也可以是4~10:1范围内的任意比值,其目的是使净化除杂渣与常压浸镍前液充分混合。
有益效果
与现有技术相比,采用上述方案本发明的有益效果为:
高冰镍中镍以两种形式存在,一种是金属相镍,另一种是非金属相镍;其中非金属相镍的含量较大,在本发明中,通过浆化和净化除杂仅仅实现了部分金属相镍与杂质发生发生置换反应而浸出,而大量的非金属相镍和剩余部分金属相镍存在于净化除杂渣中;为了实现对净化除杂渣中镍的回收,所以在本发明中还需要继续对净化除杂渣进行浆化,然后依次采用常压浸镍和加压浸镍的方式使镍浸出到加压浸出后液中,实现对高冰镍中镍的回收,避免产生废液的同时,实现镍钴浸出率达到98%以上;净化除杂产生的硫酸镍钴溶液中Ni≥90g/L,Cu≤0.01g/L、Fe≤0.01g/L;加压浸出渣中含有不到1%的镍,而铁的含量达到55%以上,这样加压浸出渣可以用于作为铁原料外销,避免废渣的产生。同时整个整备工艺中也没有废气的产生。
附图说明
图1是本发明提供的一种从高冰镍中提取硫酸镍的方法的流程图。
本发明的最佳实施方式
为了能够更清楚地理解本发明的上述目的、特征和优点等,下面结合具体实施方式对本发明进行进一步的详细描述。需要说明的是,在不冲突的情况下,本申请的实施例及实施例中的特征可以相互组合。
如图1所示,本发明提供了一种从高冰镍中提取硫酸镍的方法,该方法包括:
采用后端工艺产出的加压浸出后液对处理后的高冰镍进行浆化,目的是为了使处理后的高冰镍与加压浸出后液充分混合;然后,对浆化后的高冰镍浆料进行净化除杂,固液分离,得到硫酸镍钴溶液和净化除杂渣,此时实现了镍钴与杂质的分离;
采用常压浸镍前液对净化除杂渣进行浆化;然后,对浆化后的净化除杂渣浆料依次进行常压浸镍和加压浸镍;最后,固液分离,得到加压浸出后液和加压浸出渣;
常压浸镍前液是通过将后端工艺的加压浸出后液、水、硫酸和硫酸铜混合得到的,其中常压浸镍前液中的Cu 2+浓度为1~20g/L。
高冰镍中镍以两种形式存在,一种是金属相镍,另一种是非金属相镍;其中非金属相镍的含量较大,在本发明中,通过浆化和净化除杂仅仅实现了部分金属相镍与杂质发生置换反应而浸出,而大量的非金属相镍和剩余部分金属相镍存在于净化除杂渣中;为了实现对非金属相镍的回收,所以在本发明中还需要继续对净化除杂渣进行浆化,然后依次采用常压浸镍和加压浸镍的方式使镍与其他杂质分离,镍进入到加压浸出后液,且加压浸出后液又返回到本发明的提取工艺中,循环往复以此来实现对高冰镍中镍的回收,避免产生废液的同时实现镍钴浸出率达到98%以上;净化除杂产生的硫酸镍钴溶液中Ni≥90g/L,Cu≤0.01g/L、Fe≤0.01g/L;加压浸出渣中含有不到1%的镍,而铁的含量达到55%以上,这样加压浸出渣可以用于作为铁原料外销,避免废渣的产生。同时整个整备工艺中也没有废气的产生。在本发明的常压浸镍前液中加入了硫酸铜,铜离子能够实现在整个生产体系中循环使用。
实施例 1
本实施例提供了一种从高冰镍中提取硫酸镍的方法,其中高冰镍来自于镍红土矿,其成分(%)为:Ni~78、Fe~1、Co~1,S~20。
从上述的高冰镍中提取硫酸镍的方法具体包括如下步骤:
S1、对高冰镍进行球磨以得到90%的物料的粒径在200目以下,待用;
采用本实施例后端工艺产出的加压浸出后液与上述球磨得到的物料混合搅拌,进行浆化,其中浆化固液比为8:1,浆化时间为1h,得到高冰镍浆料;
S2、将高冰镍浆料加入到净化除杂槽中,将压缩空气或富氧空气通入净化除杂槽中,整个净化除杂反应过程中控制温度80℃,通风量1500NM 3/t物料,时间6h,反应终点pH值6.0。净化除杂后的矿浆进行固液分离,得到硫酸镍钴溶液和净化除杂渣;
S3、首先,将后端工艺产出的加压浸出后液与硫酸、硫酸铜、水混合,配置成常压浸镍前液,且常压浸镍前液中Cu 2+浓度为8g/L;
然后,将常压浸镍前液与净化除杂渣混合搅拌进行浆化,控制浆化固液比为9:1,浆化时间为1h,得到净化除杂渣浆料;
S4、将净化除杂渣浆料加入常压浸镍槽中,将压缩空气或富氧空气通入常压浸镍槽,控制整个常压浸镍过程中温度80℃,通风量1500NM 3/t物料,时间5 h,反应终点pH值1.8,其中通过控制硫酸的加入量来控制常压浸镍反应终点pH;
S5、将经过常压浸镍后的矿料加入到加压浸镍釜中,通入氧气作为反应的氧化剂,控制反应温度为165℃,反应时间为6h,氧分压为0.5 Mpa,反应终点pH值1.5;然后对加压浸出后矿浆进行固液分离,得到加压浸出后液和加压浸出渣,其中加压浸出后液返净化除杂浆化配料和常压浸镍浆化配料,而加压浸出渣作为铁原料外销。
经过上述过程处理后,各段物料成分如下:
硫酸镍钴溶液(g/L):Ni 96.38,Cu 0.006,Fe 0.003,Co 1.26。
加压浸出渣(%):Fe 57.29,Ni 0.81
Ni、Co浸出率≥98%
渣率~3.5%。
实施例 2
本实施例提供了一种从高冰镍中提取硫酸镍的方法,其中高冰镍来自于镍红土矿,其成分(%)为:Ni~75、Fe~1、Co~1,S~22。
从上述的高冰镍中提取硫酸镍的方法具体包括如下步骤:
S1、对高冰镍进行球磨以得到90%的物料的粒径在200目以下,待用;
采用本实施例后端工艺产出的加压浸出后液与上述球磨得到的物料混合搅拌,进行浆化,其中浆化固液比为7:1,浆化时间为1h,得到高冰镍浆料;
S2、将高冰镍浆料加入到净化除杂槽中,将压缩空气或富氧空气通入净化除杂槽中,整个净化除杂反应过程中控制温度85℃,通风量1800NM 3/t物料,时间6.5h,反应终点pH值6.2。净化除杂后的矿浆进行固液分离,得到硫酸镍钴溶液和净化除杂渣;
S3、首先,将后端工艺产出的加压浸出后液与硫酸、硫酸铜、水混合,配置成常压浸镍前液,且常压浸镍前液中Cu 2+浓度为10g/L;
然后,将常压浸镍前液与净化除杂渣混合搅拌进行浆化,控制浆化固液比为8:1,浆化时间为1h,得到净化除杂渣浆料;
S4、将净化除杂渣浆料加入常压浸镍槽中,将压缩空气或富氧空气通入常压浸镍槽,控制整个常压浸镍过程中温度85℃,通风量1800NM 3/t物料,时间5.5 h,反应终点pH值2.0,其中通过控制硫酸的加入量来控制常压浸镍反应终点pH;
S5、将经过常压浸镍后的矿料加入到加压浸镍釜中,通入氧气作为反应的氧化剂,控制反应温度为170℃,反应时间为6h,氧分压为0.4 Mpa,反应终点pH值1.8;然后对加压浸出后矿浆进行固液分离,得到加压浸出后液和加压浸出渣,其中加压浸出后液返净化除杂浆化配料和常压浸镍浆化配料,而加压浸出渣作为铁原料外销。
经过上述过程处理后,各段物料成分如下:
硫酸镍钴溶液(g/L):Ni 101.65,Cu 0.0001,Fe 0.001,Co 1.48。
加压浸出渣(%):Fe 59.68,Ni 0.85
Ni、Co浸出率≥98%
渣率~3.0%。
以上所述,仅为本发明较佳的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,可轻易想到的变化或替换,都应涵盖在本发明的保护范围之内。因此,本发明的保护范围应该以权利要求的保护范围为准。

Claims (10)

  1. 一种从高冰镍中提取硫酸镍的方法,其特征在于,该方法包括:
    采用后端工艺产出的加压浸出后液对处理后的高冰镍进行浆化;然后,对浆化后的高冰镍浆料进行净化除杂,固液分离,得到硫酸镍钴溶液和净化除杂渣;
    采用常压浸镍前液对所述净化除杂渣进行浆化;然后,对浆化后的净化除杂渣浆料依次进行常压浸镍和加压浸镍;最后,固液分离,得到加压浸出后液和加压浸出渣;
    所述常压浸镍前液是通过将后端工艺的加压浸出后液、水、硫酸和硫酸铜混合得到的,其中所述常压浸镍前液中的Cu 2+浓度为1~20g/L。
  2. 根据权利要求1所述的从高冰镍中提取硫酸镍的方法,其特征在于,所述净化除杂的过程包括:向浆化后的高冰镍浆料中加入氧化剂,并控制净化除杂的反应终点pH为4.0~6.5。
  3. 根据权利要求2所述的从高冰镍中提取硫酸镍的方法,其特征在于,所述净化除杂的过程中控制反应温度60~90℃,通风量500~2500NM 3/t物料,反应时间3~8h。
  4. 根据权利要求2所述的从高冰镍中提取硫酸镍的方法,其特征在于,向浆化后的高冰镍浆料中加入氧化剂具体包括:向浆化后的高冰镍浆料中通入压缩空气或富氧空气。
  5. 根据权利要求1所述的从高冰镍中提取硫酸镍的方法,其特征在于,所述常压浸镍的过程包括:将压缩空气或富氧空气通入到浆化后的净化除杂渣浆料中,并通过控制硫酸的加入量来控制反应终点的pH值为0.5~3.5。
  6. 根据权利要求5所述的从高冰镍中提取硫酸镍的方法,其特征在于,所述常压浸镍的过程中还控制反应温度60~90℃,通风量500~2500NM 3/t物料,时间3~8h。
  7. 根据权利要求1所述的从高冰镍中提取硫酸镍的方法,其特征在于,所述加压浸出过程包括:将氧化剂加入到常压浸镍后的矿浆中,控制温度为130~220℃,反应时间为2h~8h,氧分压为0.1~1.5 Mpa,反应终点pH值1.0~3.5。
  8. 根据权利要求7所述的从高冰镍中提取硫酸镍的方法,其特征在于,将氧化剂加入到常压浸镍后的矿浆中包括:将氧气通入到常压浸镍后的矿浆中。
  9. 根据权利要求1-8任一项所述的从高冰镍中提取硫酸镍的方法,其特征在于,采用后端工艺产出的加压浸出后液对处理后的高冰镍进行浆化的过程中,控制浆化固液比为4~10:1,浆化时间为0.5~2h。
  10. 根据权利要求1-8任一项所述的从高冰镍中提取硫酸镍的方法,其特征在于,采用常压浸镍前液对所述净化除杂渣进行浆化的过程中,控制浆化固液比为4~10:1,浆化时间为0.5~2h。
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