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WO2025000369A1 - Silicon removal method and silicon reutilization method in mixed hydroxide precipitate leaching process - Google Patents

Silicon removal method and silicon reutilization method in mixed hydroxide precipitate leaching process Download PDF

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Publication number
WO2025000369A1
WO2025000369A1 PCT/CN2023/104003 CN2023104003W WO2025000369A1 WO 2025000369 A1 WO2025000369 A1 WO 2025000369A1 CN 2023104003 W CN2023104003 W CN 2023104003W WO 2025000369 A1 WO2025000369 A1 WO 2025000369A1
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Prior art keywords
leaching
nickel
acid
silicon
leaching process
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PCT/CN2023/104003
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French (fr)
Chinese (zh)
Inventor
许开华
杨健
张坤
彭亚光
金国泉
刘文泽
许鹏云
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Pt Gem Indonesia New Energy Materials
Pt Qmb New Energy Materials
GEM Co Ltd Korea
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Pt Gem Indonesia New Energy Materials
Pt Qmb New Energy Materials
GEM Co Ltd Korea
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Priority to PCT/CN2023/104003 priority Critical patent/WO2025000369A1/en
Priority to CN202380010003.0A priority patent/CN117083402B/en
Publication of WO2025000369A1 publication Critical patent/WO2025000369A1/en
Pending legal-status Critical Current
Anticipated expiration legal-status Critical

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    • 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

  • Nickel cobalt hydroxide is an intermediate product of laterite nickel ore hydrometallurgy. Since laterite nickel ore contains a large amount of silicon, some silicon will inevitably be introduced into the nickel cobalt hydroxide product during the hydrometallurgical treatment process. In the subsequent acid leaching process, the silicon entrained in nickel cobalt hydroxide will be leached into the leachate, so effective means are needed to remove it.
  • the existing process for removing silicon from nickel-cobalt hydroxide leachate is mainly to remove it by forming silicic acid or silicate precipitation.
  • Existing silicon removal technologies can effectively remove silicon from the solution, but there is also the problem that silicic acid or silicates are difficult to filter, resulting in a large amount of nickel and cobalt being entrained and lost, reducing the effective utilization rate of nickel and cobalt, and significantly prolonging the processing time of the entire process.
  • the purpose of the present invention is to overcome the above-mentioned technical deficiencies and propose a method for desiliconization and silicon recycling in the process of nickel cobalt hydroxide leaching, so as to solve the technical problems in the prior art that the silicon removal technology of nickel cobalt hydroxide leaching is difficult to filter, easily leads to a large amount of nickel and cobalt loss, and has a high silicon residue in the liquid after silicon removal.
  • the present invention provides a method for desiliconization during nickel cobalt hydroxide leaching, comprising the following steps: leaching nickel cobalt hydroxide with low acid and high pressure, filtering to obtain a first filter residue and a first filtrate; wherein, during the low acid and high pressure leaching, the pH value during the leaching process is controlled to be maintained at 0.8-2.2, and the leaching temperature is 150-350°C.
  • the present invention provides a method for recycling silicon in a nickel-cobalt hydroxide leaching process.
  • the method comprises the following steps: mixing the first filter residue obtained by leaching nickel cobalt hydroxide with low acid and high pressure, further leaching the second filter residue obtained by leaching with high acid and normal pressure with a lithium source, and then calcining at high temperature to obtain a porous CaO ⁇ Li 4 SiO 4 adsorbent.
  • the beneficial effects of the present invention include:
  • the present invention converts silicic acid, which is difficult to filter, into silicon dioxide, which is easy to filter, by converting silicic acid into silicon dioxide under high temperature and high pressure, and greatly improves the filtering performance of impure silicon precipitation, thereby solving the current situation that this process causes a bottleneck in the entire production process.
  • the content of nickel and cobalt entrained in the filter residue is significantly reduced, and the silicon concentration in the leaching solution can reach less than 1ppm, which is much better than the current situation that the residual silicon in the solution is still more than 50ppm when using silicic acid to filter.
  • the nickel-cobalt hydroxide desiliconized slag obtained by high-acid and normal-pressure leaching has a high purity, and the content of entrained nickel and cobalt is less than 0.01%, which can be used as one of the synthetic materials for CO2 capture agent.
  • the present invention further synthesizes CaO ⁇ Li4SiO4 capture agent based on this, realizing the high-value utilization of silicon slag.
  • FIG1 is a process flow chart of an embodiment of a method for desiliconization and silicon recycling in a nickel-cobalt hydroxide leaching process provided by the present invention.
  • the present invention provides a method for desiliconization in the process of nickel cobalt hydroxide leaching, comprising the following steps: low acid high pressure leaching: nickel cobalt hydroxide is leached by low acid high pressure, and filtered to obtain a first filter residue and a first filtrate. The first filtrate is a nickel cobalt solution.
  • low acid high pressure leaching process is carried out in a high pressure reactor.
  • the pH value during the leaching process is controlled to be maintained at 0.8-2.2, including but not limited to 0.8, 1, 1.2, 1.3, 1.5, 1.7, 1.8, 2, 2.2, etc., preferably 1.3-2.2;
  • the leaching temperature is 150-350°C, including but not limited to 150°C, 180°C, 200°C, 250°C, 300°C, 350°C, etc., preferably 180-350°C;
  • the leaching time is 0.5-5h, including but not limited to 0.5h, 1h, 2h, 3h, 4h, 5h, etc.
  • the leaching solid-liquid ratio is controlled at 50-200g/L, Including but not limited to 50g/L, 100g/L, 150g/L, 200g/L, etc. If the solid-liquid ratio is too low, the processing volume will be affected; if the solid-liquid ratio is too high, the slurry viscosity will be too high to affect the leaching process; acid or alkali is used to adjust the pH, the acid used is a common inorganic acid, and the alkali used is calcium oxide or calcium carbonate slurry.
  • the present invention converts silicic acid into silicon dioxide under high temperature and high pressure, so that the difficult-to-filter silicic acid is transformed into easy-to-filter silicon dioxide, thereby solving the problem that this process causes a bottleneck in the entire production process.
  • the filtration performance of impure silicon precipitation is greatly improved, and the silicon concentration in the leachate can reach less than 1ppm, which is far better than the current situation where the residual silicon in the solution filtered by silicic acid is still more than 50ppm.
  • the nickel cobalt hydroxide is obtained by sequentially subjecting laterite nickel ore to high pressure acid leaching, neutralization and impurity removal, and neutralization and precipitation of nickel and cobalt. This is prior art and will not be elaborated in detail in the present invention.
  • the composition of nickel cobalt hydroxide is: Ni: 35-40%, Co 3-5%, Mn 5-10%, Fe ⁇ 0.1%, Al ⁇ 0.1%, Zn 0.5-1%, Si 0.1-0.3%.
  • the method for desiliconization in the above nickel-cobalt hydroxide leaching process also includes: a high-acid normal pressure leaching step.
  • the first filter residue is further leached with high acid and normal pressure, and the leaching acidity is controlled to be 0.1-1 mol/L, including but not limited to 0.1 mol/L, 0.2 mol/L, 0.3 mol/L, 0.4 mol/L, 0.5 mol/L, 1 mol/L, etc., preferably 0.2-0.5 mol/L;
  • the leaching temperature is room temperature, and the leaching time is 0.5-5h, including but not limited to 0.5h, 1h, 2h , 3h, 4h, 5h, etc.
  • the present invention provides a method for recycling silicon in the process of nickel cobalt hydroxide leaching, comprising the following steps: after uniformly mixing the second filter residue with the lithium source, high-temperature roasting is performed to obtain a porous CaO ⁇ Li 4 SiO 4 adsorbent.
  • the second filter residue can be dried;
  • the lithium source is lithium hydroxide or lithium carbonate;
  • the mass ratio of the second filter residue to the lithium source is 1: (1-5), including but not limited to 1: 1, 1: 2, 1: 3, 1: 4, 1: 5, etc.;
  • the temperature of high-temperature roasting is 800-1200°C, including but not limited to 800°C, 900°C, 1000°C, 1100°C, 1200°C, etc.;
  • the time of high-temperature roasting is 1: 1: 2, 1: 3, 1: 4, 1: 5, etc.
  • the calcination time is 1-5h, including but not limited to 1h, 2h, 3h, 4h, 5h, etc.; the calcination atmosphere is the atmospheric atmosphere, and the calcination product is crushed and sieved after the calcination is completed to obtain a CO2 capture agent with a particle size of less than 150 mesh.
  • the calcination tail gas generated in this step is absorbed by an alkaline solution, and further evaporated and crystallized to prepare an alkali metal sulfate or ammonium sulfate salt.
  • the present invention does not limit the type of alkali used, and those skilled in the art can choose according to actual conditions. For example, it can be an alkali metal hydroxide, ammonia water, etc., with a concentration of 1-3 mol/L.
  • the present invention mixes and roasts the second filter residue with a lithium source to further increase the value of SiO 2 /CaSO 4 residue and recycle it to prepare a porous CO 2 adsorbent (CaO ⁇ Li 4 SiO 4 adsorbent), which can be used to adsorb CO 2 in the air.
  • Low-acid high-pressure leaching In a high-pressure reactor, nickel cobalt hydroxide is leached at a solid-liquid ratio of 100g/L, a temperature of 180°C, and a time of 1h. The rotation speed is uniformly set to 400rpm during the leaching process. Dilute sulfuric acid/second filtrate or liquid alkali is continuously pumped in by a peristaltic pump to maintain the pH of the solution in the leaching reactor at 1.5 ⁇ 0.2. After the reaction is completed, the first filtrate is filtered to obtain a subsequent treatment process.
  • High-acid atmospheric pressure leaching The first filter residue is further subjected to high-acid atmospheric pressure leaching under the following conditions: solid-liquid ratio of 100 g/L, room temperature, acidity of 0.2 mol/L H 2 SO 4 , leaching time of 1 h, stirring speed uniformly set at 400 rpm. After the leaching is completed, the second filtrate and the second filter residue are obtained by filtration, wherein the second filtrate is returned to the low-acid high-pressure leaching process section to realize further utilization of the residual acid in the second filtrate.
  • Example 2-5 verifies the effect of pH on the silicon content in the first filtrate and the nickel and cobalt content entrained in the second filter residue in the low-acid high-pressure leaching step. Compared with Example 1, the only difference is that the pH is different in the low-acid high-pressure leaching step. The test results are shown in Table 1.
  • Examples 6-11 verify the effect of leaching temperature on the silicon content in the first filtrate and the nickel and cobalt content entrained in the second filter residue in the low-acid high-pressure leaching step. Compared with Example 1, the only difference is that the leaching temperature is different in the low-acid high-pressure leaching step.
  • the test results are shown in Table 2.
  • Examples 12-16 verify the effect of acidity on the content of nickel and cobalt entrained in the second filter residue in the high-acid and normal-pressure leaching step. Compared with Example 1, the only difference is that the acidity is different in the high-acid and normal-pressure leaching step.
  • the test results are shown in Table 3.
  • Step (1) of Comparative Example 1 is an existing low-acid atmospheric pressure leaching process, which is specifically as follows:
  • High-acid atmospheric pressure leaching The first filter residue is further subjected to high-acid atmospheric pressure leaching under the following conditions: solid-liquid ratio of 100 g/L, room temperature, acidity of 0.2 mol/L H 2 SO 4 , leaching time of 1 h, stirring speed uniformly set at 400 rpm. After the leaching is completed, the second filtrate and the second filter residue are obtained by filtration, wherein the second filtrate is returned to the low-acid high-pressure leaching process section to realize further utilization of the residual acid in the second filtrate.
  • the silicon content in the obtained first filtrate is 53 ppm
  • the nickel content entrained in the second filter residue is 0.58%
  • the cobalt content entrained in the second filter residue is 0.33%.
  • the present invention reduces the silicon concentration in the nickel cobalt hydroxide leaching solution to below 1ppm through one-step deep silicon removal, and greatly improves the filtering performance of the silicon removal slag; at the same time, the acid utilization rate of the whole process exceeds 95%, and the nickel and cobalt leaching rates exceed 99%.
  • the nickel cobalt hydroxide desiliconized slag has a high purity, and the entrained nickel and cobalt content is less than 0.01%, which can be used as one of the synthetic materials for CO2 capture agents.
  • the present invention further synthesizes CaO ⁇ Li4SiO4 capture agents based on this, realizing the high-value utilization of silicon slag.

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Abstract

The present invention relates to the technical field of hydrometallurgy. Disclosed are a silicon removal method and silicon reutilization method in a mixed hydroxide precipitate leaching process. The silicon removal method comprises: performing low-acid high-pressure leaching on a mixed hydroxide precipitate, and performing filtration to obtain a first filter residue and a first filtrate. According to the present invention, by converting silicic acid into silicon dioxide at high temperature and high pressure, the silicic acid which is difficult to filter is transformed into the silicon dioxide which can be easily filtered, such that the filtering performance of impurity silicon precipitates is greatly improved, thereby solving the current situation that the whole production process is stuck in the step; and additionally, the concentration of silicon in a leaching solution can reach 1 ppm or below, and the effect is far superior to that in the current situation that the concentration of residual silicon in a silicic acid filtering solution is 50 ppm or above. In addition, the silicon-removed slag of the mixed hydroxide precipitate obtained further by means of high-acid normal-pressure leaching has relatively high purity, and the content of entrained nickel and the content of entrained cobalt are both 0.01% or below, and on this basis, a CaO·Li4SiO4 trapping agent is further synthesized in the present invention, thereby achieving high-value reutilization of silicon slag.

Description

一种氢氧化镍钴浸出过程中脱硅及硅再利用的方法A method for desiliconization and silicon recycling in nickel-cobalt hydroxide leaching process 技术领域Technical Field

本发明涉及湿法冶金技术领域,尤其是涉及一种氢氧化镍钴浸出过程中脱硅及硅再利用的方法。The invention relates to the technical field of hydrometallurgy, and in particular to a method for desiliconization and silicon recycling in a nickel-cobalt hydroxide leaching process.

背景技术Background Art

氢氧化镍钴(MHP)是红土镍矿湿法冶炼的中间产品,由于红土镍矿中含有大量的硅元素,在湿法冶金处理过程中不可避免的会引入一部分硅进入到氢氧化镍钴产品中。氢氧化镍钴在后续的酸浸出过程中其中夹带的硅会一同被浸出进入到浸出液中,故需要有效的手段进行去除。Nickel cobalt hydroxide (MHP) is an intermediate product of laterite nickel ore hydrometallurgy. Since laterite nickel ore contains a large amount of silicon, some silicon will inevitably be introduced into the nickel cobalt hydroxide product during the hydrometallurgical treatment process. In the subsequent acid leaching process, the silicon entrained in nickel cobalt hydroxide will be leached into the leachate, so effective means are needed to remove it.

现有的从氢氧化镍钴浸出液中去除硅的工艺主要为通过形成硅酸或硅酸盐沉淀的方式去除。现有除硅技术手段可以有效的去除溶液中的硅,但同时也存在硅酸或硅酸盐难过滤的问题,导致大量的镍钴被夹带损失,降低镍钴的有效利用率,且会大幅度延长整个工艺流程的处理时间。此外,采用单独的硅酸或硅酸盐沉淀除硅,由于硅酸或者硅酸盐可以在水中微溶,导致除硅后液中硅残留仍然在较高的一个水平,需要进一步过树脂或者萃取的方式深度除硅,增加了整个工艺流程的处理成本和控制难度。The existing process for removing silicon from nickel-cobalt hydroxide leachate is mainly to remove it by forming silicic acid or silicate precipitation. Existing silicon removal technologies can effectively remove silicon from the solution, but there is also the problem that silicic acid or silicates are difficult to filter, resulting in a large amount of nickel and cobalt being entrained and lost, reducing the effective utilization rate of nickel and cobalt, and significantly prolonging the processing time of the entire process. In addition, the use of separate silicic acid or silicate precipitation to remove silicon, because silicic acid or silicates can be slightly soluble in water, leads to a high level of silicon residue in the liquid after silicon removal, and further deep silicon removal by resin or extraction is required, which increases the processing cost and control difficulty of the entire process.

发明内容Summary of the invention

本发明的目的在于克服上述技术不足,提出一种氢氧化镍钴浸出过程中脱硅及硅再利用的方法,解决现有技术中氢氧化镍钴浸出除硅技术过滤困难、容易导致大量镍钴损失且除硅后液中硅残留高的技术问题。The purpose of the present invention is to overcome the above-mentioned technical deficiencies and propose a method for desiliconization and silicon recycling in the process of nickel cobalt hydroxide leaching, so as to solve the technical problems in the prior art that the silicon removal technology of nickel cobalt hydroxide leaching is difficult to filter, easily leads to a large amount of nickel and cobalt loss, and has a high silicon residue in the liquid after silicon removal.

第一方面,本发明提供一种氢氧化镍钴浸出过程中脱硅的方法,包括以下步骤:将氢氧化镍钴采用低酸高压浸出,过滤得到第一滤渣和第一滤液;其中,低酸高压浸出过程中,控制浸出过程中的pH维持在0.8-2.2,浸出温度为150-350℃。In a first aspect, the present invention provides a method for desiliconization during nickel cobalt hydroxide leaching, comprising the following steps: leaching nickel cobalt hydroxide with low acid and high pressure, filtering to obtain a first filter residue and a first filtrate; wherein, during the low acid and high pressure leaching, the pH value during the leaching process is controlled to be maintained at 0.8-2.2, and the leaching temperature is 150-350°C.

第二方面,本发明提供一种氢氧化镍钴浸出过程中硅再利用的方法, 包括以下步骤:将氢氧化镍钴采用低酸高压浸出所得第一滤渣进一步采用高酸常压浸出获得的第二滤渣与锂源混合均匀后进行高温焙烧,得到多孔CaO·Li4SiO4吸附剂。In a second aspect, the present invention provides a method for recycling silicon in a nickel-cobalt hydroxide leaching process. The method comprises the following steps: mixing the first filter residue obtained by leaching nickel cobalt hydroxide with low acid and high pressure, further leaching the second filter residue obtained by leaching with high acid and normal pressure with a lithium source, and then calcining at high temperature to obtain a porous CaO·Li 4 SiO 4 adsorbent.

与现有技术相比,本发明的有益效果包括:Compared with the prior art, the beneficial effects of the present invention include:

本发明通过在高温高压下将硅酸转化为二氧化硅使难以过滤的硅酸转型为易过滤的二氧化硅,杂质硅沉淀的过滤性能大幅度改善,从而解决了该工序对整个生产工艺流程造成卡壳的现状。滤渣中夹带的镍、钴含量显著降低,且浸出液中的硅浓度可达到1ppm以下,效果远超采用硅酸过滤溶液中残留硅仍有50ppm以上的现状。此外,进一步通过高酸常压浸出获得的氢氧化镍钴脱硅渣具有较高的纯度,夹带的镍、钴含量均在0.01%以下,可作为CO2捕集剂的合成材料之一,本发明进一步以此为基础合成了CaO·Li4SiO4捕集剂,实现了硅渣的高值化利用。The present invention converts silicic acid, which is difficult to filter, into silicon dioxide, which is easy to filter, by converting silicic acid into silicon dioxide under high temperature and high pressure, and greatly improves the filtering performance of impure silicon precipitation, thereby solving the current situation that this process causes a bottleneck in the entire production process. The content of nickel and cobalt entrained in the filter residue is significantly reduced, and the silicon concentration in the leaching solution can reach less than 1ppm, which is much better than the current situation that the residual silicon in the solution is still more than 50ppm when using silicic acid to filter. In addition, the nickel-cobalt hydroxide desiliconized slag obtained by high-acid and normal-pressure leaching has a high purity, and the content of entrained nickel and cobalt is less than 0.01%, which can be used as one of the synthetic materials for CO2 capture agent. The present invention further synthesizes CaO· Li4SiO4 capture agent based on this, realizing the high-value utilization of silicon slag.

附图说明BRIEF DESCRIPTION OF THE DRAWINGS

图1是本发明提供的一种氢氧化镍钴浸出过程中脱硅及硅再利用的方法一实施方式的工艺流程图。FIG1 is a process flow chart of an embodiment of a method for desiliconization and silicon recycling in a nickel-cobalt hydroxide leaching process provided by the present invention.

具体实施方式DETAILED DESCRIPTION

为了使本发明的目的、技术方案及优点更加清楚明白,以下结合附图及实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅仅用以解释本发明,并不用于限定本发明。In order to make the purpose, technical solution and advantages of the present invention more clearly understood, the present invention is further described in detail below in conjunction with the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are only used to explain the present invention and are not intended to limit the present invention.

请参阅图1,第一方面,本发明提供一种氢氧化镍钴浸出过程中脱硅的方法,包括以下步骤:低酸高压浸出:将氢氧化镍钴采用低酸高压浸出,过滤得到第一滤渣和第一滤液。其中,第一滤液为含镍钴溶液。低酸高压浸出过程在高压反应釜中进行。该步骤中,控制浸出过程中的pH维持在0.8-2.2,包括但不限于0.8、1、1.2、1.3、1.5、1.7、1.8、2、2.2等,优选为1.3-2.2;浸出温度为150-350℃,包括但不限于150℃、180℃、200℃、250℃、300℃、350℃等,优选为180-350℃;浸出时间为0.5-5h,包括但不限于0.5h、1h、2h、3h、4h、5h等,若浸出时间过短则浸出不完全,硅去除效果差;若浸出时间过长则增大能耗;浸出固液比控制在50-200g/L, 包括但不限于50g/L、100g/L、150g/L、200g/L等,若固液比过低则影响处理量;若固液比过高则导致浆料粘稠度太大影响浸出进行;采用酸或碱调节pH,所用酸为常用无机酸,所用碱为氧化钙或碳酸钙浆料。浸出完成后,第一滤液进行后续处理工艺,第一滤渣进行下一步高酸常压浸出处理。Please refer to Figure 1. In the first aspect, the present invention provides a method for desiliconization in the process of nickel cobalt hydroxide leaching, comprising the following steps: low acid high pressure leaching: nickel cobalt hydroxide is leached by low acid high pressure, and filtered to obtain a first filter residue and a first filtrate. The first filtrate is a nickel cobalt solution. The low acid high pressure leaching process is carried out in a high pressure reactor. In this step, the pH value during the leaching process is controlled to be maintained at 0.8-2.2, including but not limited to 0.8, 1, 1.2, 1.3, 1.5, 1.7, 1.8, 2, 2.2, etc., preferably 1.3-2.2; the leaching temperature is 150-350°C, including but not limited to 150°C, 180°C, 200°C, 250°C, 300°C, 350°C, etc., preferably 180-350°C; the leaching time is 0.5-5h, including but not limited to 0.5h, 1h, 2h, 3h, 4h, 5h, etc. If the leaching time is too short, the leaching is incomplete and the silicon removal effect is poor; if the leaching time is too long, the energy consumption is increased; the leaching solid-liquid ratio is controlled at 50-200g/L, Including but not limited to 50g/L, 100g/L, 150g/L, 200g/L, etc. If the solid-liquid ratio is too low, the processing volume will be affected; if the solid-liquid ratio is too high, the slurry viscosity will be too high to affect the leaching process; acid or alkali is used to adjust the pH, the acid used is a common inorganic acid, and the alkali used is calcium oxide or calcium carbonate slurry. After the leaching is completed, the first filtrate is subjected to the subsequent treatment process, and the first filter residue is subjected to the next step of high-acid and normal-pressure leaching treatment.

本发明通过在高温高压下将硅酸反应转化为二氧化硅,使难以过滤的硅酸转型为易过滤的二氧化硅,从而解决了该工序对整个生产工艺流程造成卡壳的现状。经改进工艺后,杂质硅沉淀的过滤性能大幅度改善,且浸出液中的硅浓度可达到1ppm以下,效果远超采用硅酸过滤溶液中残留硅仍有50ppm以上的现状。The present invention converts silicic acid into silicon dioxide under high temperature and high pressure, so that the difficult-to-filter silicic acid is transformed into easy-to-filter silicon dioxide, thereby solving the problem that this process causes a bottleneck in the entire production process. After the improved process, the filtration performance of impure silicon precipitation is greatly improved, and the silicon concentration in the leachate can reach less than 1ppm, which is far better than the current situation where the residual silicon in the solution filtered by silicic acid is still more than 50ppm.

本实施方式中,上述氢氧化镍钴通过将红土镍矿依次进行高压酸浸、中和除杂、中和沉淀镍钴得到。此为现有技术,本发明对此不作赘述。In this embodiment, the nickel cobalt hydroxide is obtained by sequentially subjecting laterite nickel ore to high pressure acid leaching, neutralization and impurity removal, and neutralization and precipitation of nickel and cobalt. This is prior art and will not be elaborated in detail in the present invention.

在本发明的一些具体实施方式中,氢氧化镍钴的组成为:Ni:35-40%、Co 3-5%、Mn 5-10%、Fe<0.1%、Al<0.1%、Zn 0.5-1%、Si 0.1-0.3%。In some specific embodiments of the present invention, the composition of nickel cobalt hydroxide is: Ni: 35-40%, Co 3-5%, Mn 5-10%, Fe<0.1%, Al<0.1%, Zn 0.5-1%, Si 0.1-0.3%.

本实施方式中,上述氢氧化镍钴浸出过程中脱硅的方法,还包括:高酸常压浸出步骤。为了使第一滤渣中的镍钴强化浸出,第一滤渣进一步采用高酸常压浸出,控制浸出酸度为0.1-1mol/L,包括但不限于0.1mol/L、0.2mol/L、0.3mol/L、0.4mol/L、0.5mol/L、1mol/L等,优选为0.2-0.5mol/L;浸出温度为常温,浸出时间0.5-5h,包括但不限于0.5h、1h、2h、3h、4h、5h等,若浸出时间过短则浸出不完全,镍钴浸出效果差;若浸出时间过长则增大能耗;浸出固液比控制在50-200g/L,若固液比过低则影响处理量;若固液比过高则导致浆料粘稠度太大影响浸出进行;所用酸为常见无机酸,第二滤液可返回低酸高压浸出工序作为下一次浸出时的浸出剂,增大酸的有效利用率,第二滤渣的主要组成为SiO2及少量的CaSO4,可作为CO2捕集剂合成材料备用。In this embodiment, the method for desiliconization in the above nickel-cobalt hydroxide leaching process also includes: a high-acid normal pressure leaching step. In order to enhance the leaching of nickel and cobalt in the first filter residue, the first filter residue is further leached with high acid and normal pressure, and the leaching acidity is controlled to be 0.1-1 mol/L, including but not limited to 0.1 mol/L, 0.2 mol/L, 0.3 mol/L, 0.4 mol/L, 0.5 mol/L, 1 mol/L, etc., preferably 0.2-0.5 mol/L; the leaching temperature is room temperature, and the leaching time is 0.5-5h, including but not limited to 0.5h, 1h, 2h , 3h, 4h, 5h, etc. If the leaching time is too short, the leaching is incomplete and the nickel-cobalt leaching effect is poor; if the leaching time is too long, the energy consumption will increase; the leaching solid-liquid ratio is controlled at 50-200g/L. If the solid-liquid ratio is too low, the processing volume will be affected; if the solid-liquid ratio is too high, the slurry viscosity will be too large to affect the leaching process; the acid used is a common inorganic acid, and the second filtrate can be returned to the low-acid high-pressure leaching process as a leaching agent for the next leaching, increasing the effective utilization rate of the acid. The second filter residue is mainly composed of SiO2 and a small amount of CaSO4 , which can be used as a CO2 capture agent synthesis material for backup.

第二方面,本发明提供一种氢氧化镍钴浸出过程中硅再利用的方法,包括以下步骤:将第二滤渣与锂源混合均匀后进行高温焙烧,得到多孔CaO·Li4SiO4吸附剂。该步骤中,将第二滤渣与锂源混合前,可将第二滤渣烘干;锂源为氢氧化锂或碳酸锂;第二滤渣与锂源的质量比为1:(1-5),包括但不限于1:1、1:2、1:3、1:4、1:5等;高温焙烧的温度为800-1200℃,包括但不限于800℃、900℃、1000℃、1100℃、1200℃等;高温焙烧的时 间为1-5h,包括但不限于1h、2h、3h、4h、5h等;焙烧气氛为大气气氛,焙烧完成后对焙烧产物破碎筛分,得到粒度小于150目CO2捕集剂。该步骤产生的焙烧尾气用碱溶液吸收,进一步蒸发结晶制备碱金属硫酸盐或硫酸铵盐。本发明对所用碱的种类不作限制,本领域技术人员可以根据实际情况进行选择。例如可以为碱金属氢氧化物、氨水等,浓度为1-3mol/L。In the second aspect, the present invention provides a method for recycling silicon in the process of nickel cobalt hydroxide leaching, comprising the following steps: after uniformly mixing the second filter residue with the lithium source, high-temperature roasting is performed to obtain a porous CaO·Li 4 SiO 4 adsorbent. In this step, before the second filter residue is mixed with the lithium source, the second filter residue can be dried; the lithium source is lithium hydroxide or lithium carbonate; the mass ratio of the second filter residue to the lithium source is 1: (1-5), including but not limited to 1: 1, 1: 2, 1: 3, 1: 4, 1: 5, etc.; the temperature of high-temperature roasting is 800-1200°C, including but not limited to 800°C, 900°C, 1000°C, 1100°C, 1200°C, etc.; the time of high-temperature roasting is 1: 1: 2, 1: 3, 1: 4, 1: 5, etc. The calcination time is 1-5h, including but not limited to 1h, 2h, 3h, 4h, 5h, etc.; the calcination atmosphere is the atmospheric atmosphere, and the calcination product is crushed and sieved after the calcination is completed to obtain a CO2 capture agent with a particle size of less than 150 mesh. The calcination tail gas generated in this step is absorbed by an alkaline solution, and further evaporated and crystallized to prepare an alkali metal sulfate or ammonium sulfate salt. The present invention does not limit the type of alkali used, and those skilled in the art can choose according to actual conditions. For example, it can be an alkali metal hydroxide, ammonia water, etc., with a concentration of 1-3 mol/L.

本发明通过将第二滤渣与锂源混合焙烧,使SiO2/CaSO4渣进一步高值化再造制备多孔的CO2吸附剂(CaO·Li4SiO4吸附剂),可以用来吸附空气中的CO2The present invention mixes and roasts the second filter residue with a lithium source to further increase the value of SiO 2 /CaSO 4 residue and recycle it to prepare a porous CO 2 adsorbent (CaO·Li 4 SiO 4 adsorbent), which can be used to adsorb CO 2 in the air.

为避免赘述,本发明以下各实施例和对比例中,现将部分原料总结如下:To avoid redundant description, some raw materials are summarized as follows in the following embodiments and comparative examples of the present invention:

氢氧化镍钴的组成为:Ni 38.53%、Co 3.42%、Mn 8.38%、Fe 0.03%、Al 0.06%、Zn 0.85%、Si 0.22%。The composition of nickel cobalt hydroxide is: Ni 38.53%, Co 3.42%, Mn 8.38%, Fe 0.03%, Al 0.06%, Zn 0.85%, Si 0.22%.

实施例1Example 1

(1)低酸高压浸出:在高压反应釜中,按固液比100g/L,温度180℃,时间1h低酸高压浸出氢氧化镍钴,浸出过程中转速统一设定为400rpm,通过蠕动泵持续性的泵入稀硫酸/第二滤液或液碱维持浸出反应釜内溶液的pH维持在1.5±0.2。反应完成后过滤得到第一滤液进行后续的处理工序。(1) Low-acid high-pressure leaching: In a high-pressure reactor, nickel cobalt hydroxide is leached at a solid-liquid ratio of 100g/L, a temperature of 180°C, and a time of 1h. The rotation speed is uniformly set to 400rpm during the leaching process. Dilute sulfuric acid/second filtrate or liquid alkali is continuously pumped in by a peristaltic pump to maintain the pH of the solution in the leaching reactor at 1.5±0.2. After the reaction is completed, the first filtrate is filtered to obtain a subsequent treatment process.

(2)高酸常压浸出:将第一滤渣进一步进行高酸常压浸出,条件为固液比100g/L,温度常温,酸度为0.2mol/L H2SO4,浸出时间1h,搅拌转速统一设定在400rpm,浸出完成后过滤得到第二滤液和第二滤渣,其中第二滤液返回低酸高压浸出工序段实现第二滤液中残酸的进一步利用。(2) High-acid atmospheric pressure leaching: The first filter residue is further subjected to high-acid atmospheric pressure leaching under the following conditions: solid-liquid ratio of 100 g/L, room temperature, acidity of 0.2 mol/L H 2 SO 4 , leaching time of 1 h, stirring speed uniformly set at 400 rpm. After the leaching is completed, the second filtrate and the second filter residue are obtained by filtration, wherein the second filtrate is returned to the low-acid high-pressure leaching process section to realize further utilization of the residual acid in the second filtrate.

(3)混锂高温焙烧:第二滤渣经烘干后按质量比1:3与碳酸锂均匀混合后焙烧,焙烧温度1000℃,焙烧时间2h,焙烧完成自然冷却至室温取出破碎筛分出粒度小于150目的CaO·Li4SiO4产品,焙烧尾气用1mol/L的氢氧化钠溶液吸收。(3) Mixed lithium high temperature roasting: The second filter residue is dried and then evenly mixed with lithium carbonate in a mass ratio of 1:3 and roasted at a temperature of 1000°C for 2 hours. After roasting, it is naturally cooled to room temperature and taken out, crushed and sieved to obtain a CaO·Li 4 SiO 4 product with a particle size of less than 150 mesh. The roasting tail gas is absorbed by a 1 mol/L sodium hydroxide solution.

实施例2-5Embodiment 2-5

实施例2-5验证低酸高压浸出步骤中,pH对第一滤液中硅含量、第二滤渣中夹带的镍钴含量的影响。与实施例1相比,区别仅在于,低酸高压浸出步骤中,pH不同。测试结果见表1。Example 2-5 verifies the effect of pH on the silicon content in the first filtrate and the nickel and cobalt content entrained in the second filter residue in the low-acid high-pressure leaching step. Compared with Example 1, the only difference is that the pH is different in the low-acid high-pressure leaching step. The test results are shown in Table 1.

表1
Table 1

通过表1可以看出,低酸高压浸出步骤中,随着pH的升高,第一滤液中硅含量呈下降趋势,第二滤渣中夹带的镍钴逐渐上升;当pH升高至1.5±0.2以上时,第一滤液中硅含量呈现微弱的上升趋势,但pH在1.3~3.2范围内均小于1ppm;当pH降低至2±0.2以下时,第二滤渣中夹带的镍钴含量均在0.01%以下。It can be seen from Table 1 that in the low-acid high-pressure leaching step, as the pH increases, the silicon content in the first filtrate shows a downward trend, and the nickel and cobalt entrained in the second filter residue gradually increases; when the pH increases to above 1.5±0.2, the silicon content in the first filtrate shows a weak upward trend, but is less than 1ppm in the pH range of 1.3 to 3.2; when the pH decreases to below 2±0.2, the nickel and cobalt contents entrained in the second filter residue are all below 0.01%.

实施例6-11Embodiment 6-11

实施例6-11验证低酸高压浸出步骤中,浸出温度对第一滤液中硅含量、第二滤渣中夹带的镍钴含量的影响。与实施例1相比,区别仅在于,低酸高压浸出步骤中,浸出温度不同。测试结果见表2。Examples 6-11 verify the effect of leaching temperature on the silicon content in the first filtrate and the nickel and cobalt content entrained in the second filter residue in the low-acid high-pressure leaching step. Compared with Example 1, the only difference is that the leaching temperature is different in the low-acid high-pressure leaching step. The test results are shown in Table 2.

表2

Table 2

通过表2可以看出,低酸高压浸出步骤中,在100-350℃范围内,温度对第二滤渣中夹带的镍钴含量影响不大,均在0.01%以下。但随着温度的升高,第一滤液中硅含量呈下降趋势;当温度升高至180℃以上时,第一滤液中硅含量趋于平缓,均小于1ppm。It can be seen from Table 2 that in the low-acid high-pressure leaching step, within the range of 100-350°C, the temperature has little effect on the content of nickel and cobalt entrained in the second filter residue, all of which are below 0.01%. However, as the temperature increases, the silicon content in the first filtrate shows a downward trend; when the temperature rises to above 180°C, the silicon content in the first filtrate tends to be flat, all less than 1ppm.

实施例12-16Examples 12-16

实施例12-16验证高酸常压浸出步骤中,酸度对第二滤渣中夹带的镍钴含量的影响。与实施例1相比,区别仅在于,高酸常压浸出步骤中,酸度不同。测试结果见表3。Examples 12-16 verify the effect of acidity on the content of nickel and cobalt entrained in the second filter residue in the high-acid and normal-pressure leaching step. Compared with Example 1, the only difference is that the acidity is different in the high-acid and normal-pressure leaching step. The test results are shown in Table 3.

表3
Table 3

通过表3可以看出,高酸常压浸出步骤中,随着酸度的增加,第二滤渣中夹带的镍钴含量呈下降趋势,当酸度提升至0.2mol/L,第二滤渣中夹带的镍钴含量趋于平缓,均在0.01%以下。It can be seen from Table 3 that in the high-acid atmospheric pressure leaching step, as the acidity increases, the nickel and cobalt content entrained in the second filter residue shows a downward trend. When the acidity is increased to 0.2 mol/L, the nickel and cobalt content entrained in the second filter residue tends to be flat, all below 0.01%.

对比例1Comparative Example 1

对比例1的步骤(1)为现有的低酸常压浸出工艺,具体如下:Step (1) of Comparative Example 1 is an existing low-acid atmospheric pressure leaching process, which is specifically as follows:

(1)低酸常压浸出:将氢氧化镍钴进行低酸常压浸出,过滤得到第一滤渣和第一滤液。其中,浸出过程中转速统一设定为400rpm,通过蠕动泵 持续性的泵入稀硫酸/第二滤液或液碱控制浸出过程中pH为1.5±0.2,控制浸出过程中温度在50℃,时间控制在2h,浸出固液比控制在100g/L;(1) Low-acid atmospheric pressure leaching: nickel cobalt hydroxide is leached at low acid atmospheric pressure, and the first filter residue and the first filtrate are obtained by filtration. The rotation speed during the leaching process is uniformly set to 400 rpm, and the peristaltic pump is used to Continuously pump in dilute sulfuric acid/second filtrate or liquid alkali to control the pH value of the leaching process to 1.5±0.2, control the temperature of the leaching process to 50℃, the time to 2h, and the leaching solid-liquid ratio to 100g/L;

(2)高酸常压浸出:将第一滤渣进一步进行高酸常压浸出,条件为固液比100g/L,温度常温,酸度为0.2mol/L H2SO4,浸出时间1h,搅拌转速统一设定在400rpm,浸出完成后过滤得到第二滤液和第二滤渣,其中第二滤液返回低酸高压浸出工序段实现第二滤液中残酸的进一步利用。(2) High-acid atmospheric pressure leaching: The first filter residue is further subjected to high-acid atmospheric pressure leaching under the following conditions: solid-liquid ratio of 100 g/L, room temperature, acidity of 0.2 mol/L H 2 SO 4 , leaching time of 1 h, stirring speed uniformly set at 400 rpm. After the leaching is completed, the second filtrate and the second filter residue are obtained by filtration, wherein the second filtrate is returned to the low-acid high-pressure leaching process section to realize further utilization of the residual acid in the second filtrate.

该方法除硅过程中,过滤极为困难,且获得的第一滤液中,硅含量为53ppm,第二滤渣中夹带的镍含量0.58%,第二滤渣中夹带的钴含量为0.33%。During the silicon removal process of this method, filtration is extremely difficult, and the silicon content in the obtained first filtrate is 53 ppm, the nickel content entrained in the second filter residue is 0.58%, and the cobalt content entrained in the second filter residue is 0.33%.

综上,本发明通过一步深度除硅使氢氧化镍钴浸出液中的硅浓度降至1ppm以下,且极大改善了除硅渣的过滤性能;同时整个过程的酸利用率超过95%,镍、钴浸出率超过99%。此外,氢氧化镍钴脱硅渣具有较高的纯度,夹带的镍、钴含量均在0.01%以下,可作为CO2捕集剂的合成材料之一,本发明进一步以此为基础合成了CaO·Li4SiO4捕集剂,实现了硅渣的高值化利用。In summary, the present invention reduces the silicon concentration in the nickel cobalt hydroxide leaching solution to below 1ppm through one-step deep silicon removal, and greatly improves the filtering performance of the silicon removal slag; at the same time, the acid utilization rate of the whole process exceeds 95%, and the nickel and cobalt leaching rates exceed 99%. In addition, the nickel cobalt hydroxide desiliconized slag has a high purity, and the entrained nickel and cobalt content is less than 0.01%, which can be used as one of the synthetic materials for CO2 capture agents. The present invention further synthesizes CaO· Li4SiO4 capture agents based on this, realizing the high-value utilization of silicon slag.

以上所述本发明的具体实施方式,并不构成对本发明保护范围的限定。任何根据本发明的技术构思所作出的各种其他相应的改变与变形,均应包含在本发明权利要求的保护范围内。 The specific implementation of the present invention described above does not constitute a limitation on the protection scope of the present invention. Any other corresponding changes and modifications made based on the technical concept of the present invention should be included in the protection scope of the claims of the present invention.

Claims (14)

一种氢氧化镍钴浸出过程中脱硅的方法,其特征在于,包括以下步骤:将氢氧化镍钴采用低酸高压浸出,过滤得到第一滤渣和第一滤液;其中,所述低酸高压浸出过程中,控制浸出过程中的pH维持在0.8-2.2,浸出温度为150-350℃。A method for desiliconization during nickel cobalt hydroxide leaching, characterized in that it comprises the following steps: leaching nickel cobalt hydroxide with low acid and high pressure, filtering to obtain a first filter residue and a first filtrate; wherein, during the low acid and high pressure leaching process, the pH value during the leaching process is controlled to be maintained at 0.8-2.2, and the leaching temperature is 150-350°C. 根据权利要求1所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述低酸高压浸出过程中,控制浸出过程中的pH维持在1.3-2.2,浸出温度为180-350℃,浸出时间为0.5-5h。The method for desiliconization in the nickel cobalt hydroxide leaching process according to claim 1 is characterized in that, during the low-acid high-pressure leaching process, the pH during the leaching process is controlled to be maintained at 1.3-2.2, the leaching temperature is 180-350°C, and the leaching time is 0.5-5h. 根据权利要求1所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述低酸高压浸出过程中,浸出固液比控制在50-200g/L。The method for desiliconization in the nickel cobalt hydroxide leaching process according to claim 1 is characterized in that, during the low-acid high-pressure leaching process, the leaching solid-liquid ratio is controlled at 50-200 g/L. 根据权利要求1所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述低酸高压浸出过程中,采用酸或碱调节pH,所用酸为常用无机酸,所用碱为氧化钙或碳酸钙浆料。The method for desiliconization in the nickel cobalt hydroxide leaching process according to claim 1 is characterized in that, during the low-acid and high-pressure leaching process, an acid or a base is used to adjust the pH, the acid used is a common inorganic acid, and the base used is calcium oxide or calcium carbonate slurry. 根据权利要求1所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述低酸高压浸出过程在高压反应釜中进行。The method for desiliconization in the nickel-cobalt hydroxide leaching process according to claim 1 is characterized in that the low-acid high-pressure leaching process is carried out in a high-pressure reactor. 根据权利要求1所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述氢氧化镍钴通过将红土镍矿依次进行高压酸浸、中和除杂、中和沉淀镍钴得到。The method for desiliconization in the leaching process of nickel-cobalt hydroxide according to claim 1 is characterized in that the nickel-cobalt hydroxide is obtained by sequentially subjecting laterite nickel ore to high-pressure acid leaching, neutralization and impurity removal, and neutralization and precipitation of nickel-cobalt. 根据权利要求1所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述氢氧化镍钴的组成为:Ni:35-40%、Co 3-5%、Mn 5-10%、Fe<0.1%、Al<0.1%、Zn 0.5-1%、Si 0.1-0.3%。The method for desiliconization in the nickel-cobalt hydroxide leaching process according to claim 1 is characterized in that the composition of the nickel-cobalt hydroxide is: Ni: 35-40%, Co 3-5%, Mn 5-10%, Fe <0.1%, Al <0.1%, Zn 0.5-1%, Si 0.1-0.3%. 根据权利要求1所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,还包括:将第一滤渣采用高酸常压浸出,过滤得到第二滤渣和第二滤液;其中,所述高酸常压浸出过程中,控制浸出酸度为0.1-1mol/L,浸出温度为常温。The method for desiliconization in the nickel-cobalt hydroxide leaching process according to claim 1 is characterized in that it also includes: leaching the first filter residue with high acid and normal pressure, filtering to obtain a second filter residue and a second filtrate; wherein, during the high acid and normal pressure leaching process, the leaching acidity is controlled to be 0.1-1 mol/L, and the leaching temperature is room temperature. 根据权利要求8所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述高酸常压浸出过程中,控制浸出酸度为0.2-0.5mol/L,浸出时间为0.5-5h。The method for desiliconization in the nickel-cobalt hydroxide leaching process according to claim 8 is characterized in that, during the high-acid normal-pressure leaching process, the leaching acidity is controlled to be 0.2-0.5 mol/L and the leaching time is 0.5-5h. 根据权利要求8所述氢氧化镍钴浸出过程中脱硅的方法,其特征在 于,所述高酸常压浸出过程中,浸出固液比控制在50-200g/L。The method for desiliconization in the nickel-cobalt hydroxide leaching process according to claim 8 is characterized in that In the high-acid and normal-pressure leaching process, the leaching solid-liquid ratio is controlled at 50-200 g/L. 根据权利要求8所述氢氧化镍钴浸出过程中脱硅的方法,其特征在于,所述第二滤液返回低酸高压浸出工序作为下一次浸出时的浸出剂。The method for desiliconization in the nickel-cobalt hydroxide leaching process according to claim 8 is characterized in that the second filtrate is returned to the low-acid high-pressure leaching process as a leaching agent for the next leaching. 一种氢氧化镍钴浸出过程中硅再利用的方法,其特征在于,包括以下步骤:将权利要求8-11中任一项所述第二滤渣与锂源混合均匀后进行高温焙烧,得到多孔CaO·Li4SiO4吸附剂。A method for recycling silicon in the process of nickel-cobalt hydroxide leaching, characterized by comprising the following steps: uniformly mixing the second filter residue according to any one of claims 8 to 11 with a lithium source and then calcining at high temperature to obtain a porous CaO·Li 4 SiO 4 adsorbent. 根据权利要求12所述氢氧化镍钴浸出过程中硅再利用的方法,其特征在于,所述锂源为氢氧化锂或碳酸锂;所述第二滤渣与锂源的质量比为1:(1-5)。The method for recycling silicon in the nickel-cobalt hydroxide leaching process according to claim 12, characterized in that the lithium source is lithium hydroxide or lithium carbonate; and the mass ratio of the second filter residue to the lithium source is 1:(1-5). 根据权利要求12所述氢氧化镍钴浸出过程中硅再利用的方法,其特征在于,所述高温焙烧的温度为800-1200℃,所述高温焙烧的时间为1-5h,焙烧气氛为大气气氛。 The method for recycling silicon in the nickel cobalt hydroxide leaching process according to claim 12 is characterized in that the temperature of the high-temperature roasting is 800-1200°C, the time of the high-temperature roasting is 1-5h, and the roasting atmosphere is the atmospheric atmosphere.
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