CN116768246A - A method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium - Google Patents

A method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium Download PDF

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CN116768246A
CN116768246A CN202310820449.1A CN202310820449A CN116768246A CN 116768246 A CN116768246 A CN 116768246A CN 202310820449 A CN202310820449 A CN 202310820449A CN 116768246 A CN116768246 A CN 116768246A
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lithium
aluminum
sulfate solution
waste residue
leaching
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杨声海
李帅
赖延清
杨亚辉
陈永明
朱容伯
刘远健
崔葵馨
田忠良
金胜明
江浩
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Central South University
Hunan Normal University
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Hunan Normal University
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D15/00Lithium compounds
    • C01D15/06Sulfates; Sulfites
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D5/00Sulfates or sulfites of sodium, potassium or alkali metals in general
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/02Aluminium oxide; Aluminium hydroxide; Aluminates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/48Halides, with or without other cations besides aluminium
    • C01F7/50Fluorides

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  • Inorganic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
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  • Processing Of Solid Wastes (AREA)

Abstract

The invention belongs to the technical field of solid waste treatment, and provides a method for efficiently separating and enriching lithium from lithium and aluminum in aluminum electrolyte waste residues, which comprises the following steps: mixing aluminum electrolyte waste residue and aluminum sulfate, and performing primary low-temperature roasting and secondary high-temperature thermal decomposition to obtain a roasting material and sulfur-containing flue gas; introducing sulfur-containing flue gas into an alkali solution to obtain a sulfate solution; leaching the roasting material with water, and filtering to obtain water leaching slag and sodium-potassium-containing lithium sulfate solution; and (3) repeating the water leaching process for a plurality of times on the lithium sulfate solution containing sodium and potassium to obtain the lithium-rich sulfate solution. The invention ensures the high-efficiency separation of lithium and aluminum in the aluminum electrolyte waste residue, realizes the recycling of aluminum fluoride, obtains the lithium-rich sulfate solution, and provides convenience for the subsequent high-efficiency recovery of high-added-value lithium salt products. The method has the advantages of simple process flow, low equipment requirement and strong practicability.

Description

一种铝电解质废渣的锂铝高效分离和富集锂的方法A method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium

技术领域Technical field

本发明涉及固体废弃物处理技术领域,尤其涉及一种铝电解质废渣的锂铝高效分离和富集锂的方法。The present invention relates to the technical field of solid waste treatment, and in particular to a method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium.

背景技术Background technique

我国一水硬铝石型铝土矿含有锂等碱金属杂质,经“氧化铝-铝电解”生产工序富集于铝电解质中,严重影响铝的电解生产。富锂铝电解质废渣是含锂一水硬铝石型铝土矿开发利用所产生的特有非传统锂资源,锂的存在形式、矿物结构等尚不明确,现有提锂技术无法适用。当前铝电解质废渣主要堆存处置,不但存在氟污染风险,而且战略资源锂得不到有效利用。my country's diaspore-type bauxite contains alkali metal impurities such as lithium, which are enriched in the aluminum electrolyte through the "alumina-aluminum electrolysis" production process, seriously affecting the electrolytic production of aluminum. Lithium-rich aluminum electrolyte waste residue is a unique non-traditional lithium resource produced by the development and utilization of lithium-containing diaspore-type bauxite. The existence form and mineral structure of lithium are not yet clear, and existing lithium extraction technology cannot be applied. At present, aluminum electrolyte waste residue is mainly stored and disposed, which not only poses the risk of fluorine pollution, but also cannot effectively utilize the strategic resource lithium.

在现有的技术中,CN113981232A公开了一种铝电解质废渣中锂元素的硫酸铝直接浸出回收方法。其方法是通过硫酸铝溶液浸出含锂铝电解质废渣,再依次通过碱解反应、碳化反应、热解得到碳酸锂;该方法使用硫酸铝溶液浸出含锂氟化物物相转化率低、流程冗长,且产生难分离的Al(OH)3胶体并影响后续提锂。CN105293536A公开了一种电解铝废渣提锂方法。其方法是将电解铝废渣通过浓硫酸焙烧、碳酸钠碱解、石灰苛化及碳化反应得到碳酸锂;该方法使用浓硫酸焙烧,对设备要求高,流程复杂,且产生难分离的Al(OH)3胶体并影响后续提锂。CN105349786A公开了一种含锂铝电解质综合回收利用的方法。其方法是将含锂铝电解质与水混合并使用无机酸调节pH<2,加入铝盐制备冰晶石,再通过碳酸钠碱解、CO2碳化、阳离子交换树脂除杂、脱CO2处理得到高纯碳酸锂。该方法使用阳离子交换树脂除杂,成本太高,且产生难分离的Al(OH)3胶体并影响后续提锂。Among the existing technologies, CN113981232A discloses a direct leaching and recovery method of aluminum sulfate for lithium elements in aluminum electrolyte waste residue. The method is to leach lithium-containing aluminum electrolyte waste residue through aluminum sulfate solution, and then obtain lithium carbonate through alkaline hydrolysis reaction, carbonization reaction, and pyrolysis in sequence; this method uses aluminum sulfate solution to leach lithium-containing fluoride with a low phase conversion rate and a lengthy process. And it produces Al(OH) 3 colloid that is difficult to separate and affects subsequent lithium extraction. CN105293536A discloses a method for extracting lithium from electrolytic aluminum waste residue. The method is to roast electrolytic aluminum waste residue through concentrated sulfuric acid roasting, sodium carbonate alkaline hydrolysis, lime causticization and carbonization reaction to obtain lithium carbonate; this method uses concentrated sulfuric acid for roasting, which has high equipment requirements, complicated processes, and produces Al(OH which is difficult to separate). ) 3 colloid and affect subsequent lithium extraction. CN105349786A discloses a method for comprehensive recycling of lithium-containing aluminum electrolytes. The method is to mix the lithium-containing aluminum electrolyte with water and use inorganic acid to adjust the pH <2, add aluminum salt to prepare cryolite, and then proceed through sodium carbonate alkaline hydrolysis, CO 2 carbonization, cation exchange resin impurity removal, and CO 2 removal to obtain a high-quality electrolyte. Pure lithium carbonate. This method uses cation exchange resin to remove impurities, which is too costly and produces Al(OH) 3 colloid that is difficult to separate and affects subsequent lithium extraction.

目前,针对铝电解工业氟化物电解质废渣的资源化利用技术尚未成熟,均未有提纯锂来进行锂铝分离的方法,造成现有的提锂工艺存在过程冗长、工艺复杂的问题。因此,开展富锂铝电解质废渣清洁回收与锂高效富集技术的研究,既可避免铝电解工业因锂等碱金属积累产生大量电解质废渣堆存和氟污染泄露的风险,也可缓解因新能源迅猛发展所带来的锂资源安全保障问题;对强化铝电解工业清洁生产,推进大宗危废综合利用,支撑新能源汽车产业发展等具有重要意义。At present, the resource utilization technology for fluoride electrolyte waste residue in the aluminum electrolysis industry is not yet mature, and there is no method to purify lithium for lithium and aluminum separation, causing the existing lithium extraction process to be lengthy and complex. Therefore, carrying out research on the clean recovery of lithium-rich aluminum electrolyte waste residue and efficient lithium enrichment technology can not only avoid the risk of large amounts of electrolyte waste residue accumulation and fluorine pollution leakage due to the accumulation of alkali metals such as lithium in the aluminum electrolysis industry, but also alleviate the risk of new energy sources. The security issues of lithium resources brought about by the rapid development are of great significance to strengthening the clean production of the aluminum electrolysis industry, promoting the comprehensive utilization of bulk hazardous waste, and supporting the development of the new energy automobile industry.

发明内容Contents of the invention

本发明的目的是针对现有技术的不足,提供一种铝电解质废渣的锂铝高效分离和富集锂的方法。The object of the present invention is to provide a method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium in view of the shortcomings of the existing technology.

为了实现上述发明目的,本发明提供以下技术方案:In order to achieve the above-mentioned object of the invention, the present invention provides the following technical solutions:

本发明提供了一种铝电解质废渣的锂铝高效分离和富集锂的方法,包括如下步骤:The invention provides a method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium, which includes the following steps:

1)将铝电解质废渣和硫酸铝混合,进行一段低温焙烧和二段高温热分解,得到焙烧料和含硫烟气;1) Mix aluminum electrolyte waste residue and aluminum sulfate, perform one stage of low-temperature roasting and two stages of high-temperature thermal decomposition, and obtain roasting materials and sulfur-containing flue gas;

2)将含硫烟气通入碱溶液中,得到硫酸盐溶液;2) Pass the sulfur-containing flue gas into the alkali solution to obtain a sulfate solution;

3)将焙烧料用水浸出后过滤,得到水浸渣和含钠钾的硫酸锂溶液;3) Leach the roasted material with water and then filter it to obtain water leaching residue and a lithium sulfate solution containing sodium and potassium;

4)将含钠钾的硫酸锂溶液返回步骤3)的水浸工序,经多次循环浸出后得到富锂硫酸盐溶液。4) Return the lithium sulfate solution containing sodium and potassium to the water leaching process in step 3), and obtain a lithium-rich sulfate solution after multiple cycles of leaching.

作为优选,步骤1)所述铝电解质废渣和硫酸铝的质量比为1:0.5~1.5。Preferably, the mass ratio of the aluminum electrolyte waste residue and aluminum sulfate described in step 1) is 1:0.5-1.5.

作为优选,步骤1)所述一段低温焙烧的温度为200~600℃,一段低温焙烧的时间为0.5~5h。Preferably, the temperature of one stage of low-temperature roasting in step 1) is 200-600°C, and the time of one stage of low-temperature roasting is 0.5-5 hours.

作为优选,步骤1)所述二段高温热分解的温度为700~1000℃,二段高温热分解的时间为0.5~3h。Preferably, the temperature of the second-stage high-temperature thermal decomposition in step 1) is 700-1000°C, and the time of the second-stage high-temperature thermal decomposition is 0.5-3 hours.

作为优选,步骤2)所述碱溶液的浓度为50~300g/L。Preferably, the concentration of the alkali solution in step 2) is 50-300g/L.

作为优选,步骤3)中,焙烧料和水的质量体积比为1g:3~15mL。Preferably, in step 3), the mass volume ratio of the roasted material and water is 1g:3-15mL.

作为优选,步骤3)所述浸出的温度为30~95℃,浸出的时间为0.5~5h。Preferably, the leaching temperature in step 3) is 30 to 95°C, and the leaching time is 0.5 to 5 hours.

作为优选,步骤4)所述多次循环浸出的次数为5~20次。Preferably, the number of multiple cycles of leaching in step 4) is 5 to 20 times.

本发明的有益效果包括以下几点:The beneficial effects of the present invention include the following points:

1)本发明提供了一种铝电解质废渣和硫酸铝经两段焙烧分解–水浸实现锂铝高效分离与富集锂的方法。本发明通过两段焙烧分解–水浸促进电解质废渣中锂钠钾钙的氟化物转化为硫酸盐物相和氟化铝,并选择性高温热分解未反应的硫酸铝,实现了含锂钠钾的可溶性硫酸盐与水浸渣中难溶含铝物相(Al2O3和AlF3)的高效浸出分离,避免了硫酸铝水解对锂回收的影响,富集后的富锂硫酸盐溶液为后续高效回收金属锂提供了便利。1) The present invention provides a method for efficiently separating lithium and aluminum and enriching lithium through two-stage roasting and decomposition of aluminum electrolyte waste residue and aluminum sulfate - water leaching. The invention promotes the conversion of lithium, sodium, potassium and calcium fluoride in electrolyte waste residue into sulfate phase and aluminum fluoride through two stages of roasting and decomposition-water immersion, and selectively high-temperature thermal decomposition of unreacted aluminum sulfate to achieve lithium-containing sodium and potassium. The efficient leaching and separation of soluble sulfate and the insoluble aluminum-containing phase (Al 2 O 3 and AlF 3 ) in the water leaching residue avoids the impact of aluminum sulfate hydrolysis on lithium recovery. The enriched lithium-rich sulfate solution is It provides convenience for subsequent efficient recovery of metallic lithium.

2)本发明通过水浸渣(Al2O3和AlF3)返回铝电解系统实现了氟化铝的资源化循环利用,避免了氟污染扩散的风险。本发明在保证铝电解质废渣中锂铝高效分离的同时,还实现了氟化铝的资源化循环利用,获得了富锂硫酸盐溶液,为后续高效回收高附加值金属锂提供了便利。2) The present invention realizes resource recycling of aluminum fluoride by returning water-leached slag (Al 2 O 3 and AlF 3 ) to the aluminum electrolysis system, thereby avoiding the risk of the spread of fluorine pollution. While ensuring efficient separation of lithium and aluminum from aluminum electrolyte waste residue, the present invention also realizes resource recycling of aluminum fluoride and obtains a lithium-rich sulfate solution, which facilitates the subsequent efficient recovery of high value-added metal lithium.

3)本发明的方法工艺流程简单,设备要求低,实用性强。3) The method of the present invention has a simple process flow, low equipment requirements and strong practicability.

附图说明Description of drawings

图1为本发明的铝电解质废渣的锂铝高效分离和富集锂的工艺流程示意图。Figure 1 is a schematic process flow diagram of the efficient separation of lithium and aluminum from aluminum electrolyte waste residue and the enrichment of lithium according to the present invention.

具体实施方式Detailed ways

本发明提供了一种铝电解质废渣的锂铝高效分离和富集锂的方法,包括如下步骤:The invention provides a method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium, which includes the following steps:

1)将铝电解质废渣和硫酸铝混合,进行一段低温焙烧和二段高温热分解,得到焙烧料和含硫烟气;1) Mix aluminum electrolyte waste residue and aluminum sulfate, perform one stage of low-temperature roasting and two stages of high-temperature thermal decomposition, and obtain roasting materials and sulfur-containing flue gas;

2)将含硫烟气通入碱溶液中,得到硫酸盐溶液;2) Pass the sulfur-containing flue gas into the alkali solution to obtain a sulfate solution;

3)将焙烧料用水浸出后过滤,得到水浸渣和含钠钾的硫酸锂溶液;3) Leach the roasted material with water and then filter it to obtain water leaching residue and a lithium sulfate solution containing sodium and potassium;

4)将含钠钾的硫酸锂溶液返回步骤3)的水浸工序,经多次循环浸出后得到富锂硫酸盐溶液。4) Return the lithium sulfate solution containing sodium and potassium to the water leaching process in step 3), and obtain a lithium-rich sulfate solution after multiple cycles of leaching.

本发明中,步骤1)所述铝电解质废渣优选为破碎处理得到的铝电解质废渣,铝电解质废渣的目数优选为100~400目,进一步优选为150~350目,更优选为200~300目;铝电解质废渣为富锂铝电解质废渣。In the present invention, the aluminum electrolyte waste residue in step 1) is preferably the aluminum electrolyte waste residue obtained by crushing treatment. The mesh number of the aluminum electrolyte waste residue is preferably 100 to 400 mesh, more preferably 150 to 350 mesh, and more preferably 200 to 300 mesh. ; Aluminum electrolyte waste residue is lithium-rich aluminum electrolyte waste residue.

本发明中,步骤1)所述铝电解质废渣和硫酸铝的质量比优选为1:0.5~1.5,进一步优选为1:0.7~1.3,更优选为1:0.8~1.2。In the present invention, the mass ratio of the aluminum electrolyte waste residue and aluminum sulfate described in step 1) is preferably 1:0.5-1.5, more preferably 1:0.7-1.3, and more preferably 1:0.8-1.2.

本发明中,步骤1)所述一段低温焙烧的温度优选为200~600℃,进一步优选为250~550℃,更优选为300~500℃;一段低温焙烧的时间优选为0.5~5h,进一步优选为1~4h,更优选为2~3h。In the present invention, the temperature of one stage of low-temperature roasting in step 1) is preferably 200~600°C, more preferably 250~550°C, more preferably 300~500°C; the time of one stage of low-temperature roasting is preferably 0.5~5h, further preferably It is 1-4h, more preferably, it is 2-3h.

本发明中,步骤1)所述二段高温热分解的温度优选为700~1000℃,进一步优选为750~950℃,更优选为800~900℃,二段高温热分解的时间优选为0.5~3h,进一步优选为1~2.5h,更优选为1.5~2h。In the present invention, the temperature of the second-stage high-temperature thermal decomposition in step 1) is preferably 700-1000°C, further preferably 750-950°C, more preferably 800-900°C, and the time of the second-stage high-temperature thermal decomposition is preferably 0.5-1000°C. 3h, more preferably 1 to 2.5h, more preferably 1.5 to 2h.

本发明中,步骤2)所述碱溶液的浓度优选为50~300g/L,进一步优选为100~250g/L,更优选为150~200g/L。In the present invention, the concentration of the alkali solution in step 2) is preferably 50-300g/L, more preferably 100-250g/L, and more preferably 150-200g/L.

本发明中,步骤2)所述碱溶液优选为氢氧化钠水溶液。In the present invention, the alkali solution in step 2) is preferably an aqueous sodium hydroxide solution.

本发明步骤3)中,焙烧料和水的质量体积比优选为1g:3~15mL,进一步优选为1g:5~12mL,更优选为1g:8~10mL。In step 3) of the present invention, the mass-volume ratio of the roasting material and water is preferably 1g:3-15mL, more preferably 1g:5-12mL, and more preferably 1g:8-10mL.

本发明中,步骤3)所述浸出的温度优选为30~95℃,进一步优选为40~90℃,更优选为50~85℃;浸出的时间优选为0.5~5h,进一步优选为1~4h,更优选为2~3h。In the present invention, the leaching temperature in step 3) is preferably 30-95°C, more preferably 40-90°C, more preferably 50-85°C; the leaching time is preferably 0.5-5h, further preferably 1-4h , more preferably 2 to 3 hours.

本发明中,步骤3)所述水浸渣中包含AlF3和Al2O3,水浸渣返回铝电解系统。In the present invention, the water leaching slag in step 3) contains AlF 3 and Al 2 O 3 , and the water leaching slag is returned to the aluminum electrolysis system.

本发明中,步骤4)所述多次循环浸出的次数优选为5~20次,进一步优选为6~18次,更优选为8~15次;所述富锂硫酸盐溶液用于净化沉锂。In the present invention, the number of multiple cycles of leaching in step 4) is preferably 5 to 20 times, more preferably 6 to 18 times, and more preferably 8 to 15 times; the lithium-rich sulfate solution is used to purify lithium precipitation. .

本发明的铝电解质废渣的锂铝高效分离和富集锂的工艺流程示意图如图1所示,其中,富锂铝电解质废渣即为本发明的铝电解质废渣。The schematic process flow diagram of the efficient separation of lithium and aluminum from the aluminum electrolyte waste residue of the present invention and the enrichment of lithium is shown in Figure 1, in which the lithium-rich aluminum electrolyte waste residue is the aluminum electrolyte waste residue of the present invention.

下面结合实施例对本发明提供的技术方案进行详细的说明,但是不能把它们理解为对本发明保护范围的限定。The technical solutions provided by the present invention will be described in detail below with reference to the examples, but they should not be understood as limiting the protection scope of the present invention.

实施例1Example 1

将100g破碎处理至400目的某电解铝厂铝电解质废渣和70g硫酸铝混合均匀,混合物在300℃进行一段低温焙烧(低温焙烧时间为4h)后在750℃进行二段高温热分解(高温热分解的时间为3h),得到焙烧料和含硫烟气。将含硫烟气通入浓度为100g/L的氢氧化钠溶液中,经吸收后得到硫酸钠溶液。将焙烧料与水(焙烧料和水的用量比为1g:5mL)混合后在温度为75℃、转速为500r/min的条件下搅拌浸出4h,过滤得到水浸渣和含钠钾的硫酸锂溶液。100g of aluminum electrolyte waste residue from an electrolytic aluminum plant and 70g of aluminum sulfate were mixed evenly after being crushed to 400 mesh. The mixture was subjected to a low-temperature roasting at 300°C (low-temperature roasting time is 4 hours) and then was subjected to a second-stage high-temperature thermal decomposition (high-temperature thermal decomposition) at 750°C. The time is 3h), and the roasted material and sulfur-containing flue gas are obtained. Pass the sulfur-containing flue gas into a sodium hydroxide solution with a concentration of 100g/L, and obtain a sodium sulfate solution after absorption. Mix the roasted material and water (the dosage ratio of roasted material and water is 1g:5mL), stir and leach for 4 hours at a temperature of 75°C and a rotation speed of 500r/min, then filter to obtain the water leaching residue and lithium sulfate containing sodium and potassium. solution.

本实施例的含钠钾的硫酸锂溶液中未检测出Al3+,Na和K的浸出率分别为95.45%和96.12%,Li的浸出率为96.48%,含钠钾的硫酸锂溶液在相同条件下经12次循环水浸后,得到的富锂硫酸盐溶液中锂含量为15g/L。No Al 3+ was detected in the lithium sulfate solution containing sodium and potassium in this example. The leaching rates of Na and K were 95.45% and 96.12% respectively. The leaching rate of Li was 96.48%. The lithium sulfate solution containing sodium and potassium was in the same After 12 cycles of water immersion under the conditions, the lithium content in the obtained lithium-rich sulfate solution was 15g/L.

实施例2Example 2

将100g破碎处理至300目的某电解铝厂铝电解质废渣和90g硫酸铝混合均匀,混合物在350℃进行一段低温焙烧(低温焙烧时间为3h)后在800℃进行二段高温热分解(高温热分解的时间为2.5h),得到焙烧料和含硫烟气。将含硫烟气通入浓度为150g/L的氢氧化钠溶液中,经吸收后得到硫酸钠溶液。将焙烧料与水(焙烧料和水的用量比为1g:7mL)混合后在温度为80℃、转速为600r/min的条件下搅拌浸出2.5h,过滤得到水浸渣和含钠钾的硫酸锂溶液。100g of aluminum electrolyte waste residue from an electrolytic aluminum plant and 90g of aluminum sulfate were mixed evenly after crushing and processing to 300 mesh. The mixture was subjected to a low-temperature roasting at 350°C (low-temperature roasting time is 3 hours) and then was subjected to a second-stage high-temperature thermal decomposition (high-temperature thermal decomposition) at 800°C. The time is 2.5h) to obtain roasted materials and sulfur-containing flue gas. Pass the sulfur-containing flue gas into a sodium hydroxide solution with a concentration of 150g/L, and obtain a sodium sulfate solution after absorption. Mix the roasted material and water (the dosage ratio of roasted material and water is 1g:7mL), stir and leach for 2.5 hours at a temperature of 80°C and a rotation speed of 600r/min, then filter to obtain the water leaching residue and sulfuric acid containing sodium and potassium. Lithium solution.

本实施例的含钠钾的硫酸锂溶液中未检测出Al3+,Na和K的浸出率分别为96.43%和96.97%,Li的浸出率为98.21%,含钠钾的硫酸锂溶液在相同条件下经10次循环水浸后,得到的富锂硫酸盐溶液中锂含量为12g/L。No Al 3+ was detected in the lithium sulfate solution containing sodium and potassium in this example. The leaching rates of Na and K were 96.43% and 96.97% respectively. The leaching rate of Li was 98.21%. The lithium sulfate solution containing sodium and potassium was in the same After 10 cycles of water immersion under the conditions, the lithium content in the obtained lithium-rich sulfate solution was 12g/L.

实施例3Example 3

将100g破碎处理至200目的某电解铝厂铝电解质废渣和120g硫酸铝混合均匀,混合物在400℃进行一段低温焙烧(低温焙烧时间为2h)后在850℃进行二段高温热分解(高温热分解的时间为1h),得到焙烧料和含硫烟气。将含硫烟气通入浓度为175g/L的氢氧化钠溶液中,经吸收后得到硫酸钠溶液。将焙烧料与水(焙烧料和水的用量比为1g:9mL)混合后在温度为85℃、转速为700r/min的条件下搅拌浸出2h,过滤得到水浸渣和含钠钾的硫酸锂溶液。100g of aluminum electrolyte waste residue from an electrolytic aluminum plant and 120g of aluminum sulfate were mixed evenly after crushing and processing to 200 mesh. The mixture was subjected to a low-temperature roasting at 400°C (low-temperature roasting time is 2 hours) and then was subjected to a second-stage high-temperature thermal decomposition (high-temperature thermal decomposition) at 850°C. The time is 1h), and the roasted material and sulfur-containing flue gas are obtained. Pass the sulfur-containing flue gas into a sodium hydroxide solution with a concentration of 175g/L, and obtain a sodium sulfate solution after absorption. Mix the roasted material and water (the dosage ratio of roasted material and water is 1g:9mL), stir and leach for 2 hours at a temperature of 85°C and a rotation speed of 700r/min, then filter to obtain the water leaching residue and lithium sulfate containing sodium and potassium. solution.

本实施例的含钠钾的硫酸锂溶液中未检测出Al3+,Na和K的浸出率分别为97.33%和97.67%,Li的浸出率为96.59%,含钠钾的硫酸锂溶液在相同条件下经8次循环水浸后,得到的富锂硫酸盐溶液中锂含量为10g/L。No Al 3+ was detected in the lithium sulfate solution containing sodium and potassium in this example. The leaching rates of Na and K were 97.33% and 97.67% respectively. The leaching rate of Li was 96.59%. The lithium sulfate solution containing sodium and potassium was in the same After 8 cycles of water immersion under the conditions, the lithium content in the obtained lithium-rich sulfate solution was 10g/L.

实施例4Example 4

将100g破碎处理至150目的某电解铝厂铝电解质废渣和140g硫酸铝混合均匀,混合物在500℃进行一段低温焙烧(低温焙烧时间为1h)后在900℃进行二段高温热分解(高温热分解的时间为1.5h),得到焙烧料和含硫烟气。将含硫烟气通入浓度为225g/L的氢氧化钠溶液中,经吸收后得到硫酸钠溶液。将焙烧料与水(焙烧料和水的用量比为1g:12mL)混合后在温度为50℃、转速为700r/min的条件下搅拌浸出3h,过滤得到水浸渣和含钠钾的硫酸锂溶液。Mix 100g of aluminum electrolyte waste residue from an electrolytic aluminum plant to 150 mesh and 140g of aluminum sulfate. The mixture is subjected to a low-temperature roasting at 500°C (low-temperature roasting time is 1 hour) and then a second-stage high-temperature thermal decomposition (high-temperature thermal decomposition) at 900°C. The time is 1.5h) to obtain roasted material and sulfur-containing flue gas. Pass the sulfur-containing flue gas into a sodium hydroxide solution with a concentration of 225g/L, and obtain a sodium sulfate solution after absorption. Mix the roasted material and water (the dosage ratio of roasted material and water is 1g:12mL), stir and leach for 3 hours at a temperature of 50°C and a rotation speed of 700r/min, then filter to obtain the water leaching residue and lithium sulfate containing sodium and potassium. solution.

本实施例的含钠钾的硫酸锂溶液中未检测出Al3+,Na和K的浸出率分别为96.89%和97.32%,Li的浸出率为97.89%,含钠钾的硫酸锂溶液在相同条件下经15次循环水浸后,得到的富锂硫酸盐溶液中锂含量为14g/L。No Al 3+ was detected in the lithium sulfate solution containing sodium and potassium in this example. The leaching rates of Na and K were 96.89% and 97.32% respectively. The leaching rate of Li was 97.89%. The lithium sulfate solution containing sodium and potassium was in the same After 15 cycles of water immersion under the conditions, the lithium content in the obtained lithium-rich sulfate solution was 14g/L.

本发明提供了一种铝电解质废渣和硫酸铝经两段焙烧分解-水浸实现锂铝高效分离与富集锂的方法。本发明通过两段焙烧分解-水浸促进电解质废渣中锂钠钾钙的氟化物转化为硫酸盐物相和氟化铝,并选择性高温热分解未反应的硫酸铝,实现了含锂钠钾的可溶性硫酸盐与难溶含铝物相(Al2O3和AlF3)的高效浸出分离,避免了硫酸铝水解对锂回收的影响,富集后的富锂硫酸盐溶液为后续高效回收金属锂提供了便利。本发明通过水浸渣(Al2O3和AlF3)返回铝电解系统实现了氟化铝的资源化循环利用,避免了氟污染扩散的风险。本发明在保证铝电解质废渣中锂铝高效分离的同时,还实现了氟化铝的资源化循环利用,获得了富锂硫酸盐溶液,为后续高效回收高附加值金属锂提供了便利。本发明的方法工艺流程简单,设备要求低,实用性强。The invention provides a method for efficiently separating lithium and aluminum and enriching lithium through two-stage roasting and decomposition of aluminum electrolyte waste residue and aluminum sulfate-water leaching. The present invention promotes the conversion of lithium, sodium, potassium and calcium fluoride in electrolyte waste residue into sulfate phase and aluminum fluoride through two stages of roasting and decomposition-water leaching, and selectively high-temperature thermal decomposition of unreacted aluminum sulfate to achieve lithium-containing sodium and potassium. Efficient leaching and separation of soluble sulfate and insoluble aluminum-containing phases (Al 2 O 3 and AlF 3 ) avoids the impact of aluminum sulfate hydrolysis on lithium recovery. The enriched lithium-rich sulfate solution provides the subsequent efficient recovery of metals. Lithium provides convenience. The present invention realizes resource recycling of aluminum fluoride by returning water-leached slag (Al 2 O 3 and AlF 3 ) to the aluminum electrolysis system, thereby avoiding the risk of fluorine pollution diffusion. While ensuring efficient separation of lithium and aluminum from aluminum electrolyte waste residue, the present invention also realizes resource recycling of aluminum fluoride and obtains a lithium-rich sulfate solution, which facilitates the subsequent efficient recovery of high value-added metal lithium. The method of the invention has simple process flow, low equipment requirements and strong practicability.

以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above are only preferred embodiments of the present invention. It should be noted that those skilled in the art can make several improvements and modifications without departing from the principles of the present invention. These improvements and modifications can also be made. should be regarded as the protection scope of the present invention.

Claims (8)

1. The method for efficiently separating and enriching lithium from lithium and aluminum in the aluminum electrolyte waste residue is characterized by comprising the following steps of:
1) Mixing aluminum electrolyte waste residue and aluminum sulfate, and performing primary low-temperature roasting and secondary high-temperature thermal decomposition to obtain a roasting material and sulfur-containing flue gas;
2) Introducing sulfur-containing flue gas into an alkali solution to obtain a sulfate solution;
3) Leaching the roasting material with water, and filtering to obtain water leaching slag and sodium-potassium-containing lithium sulfate solution;
4) And returning the lithium sulfate solution containing sodium and potassium to the water leaching process of the step 3), and circularly leaching for a plurality of times to obtain the lithium-rich sulfate solution.
2. The method according to claim 1, wherein the mass ratio of the aluminum electrolyte waste residue to aluminum sulfate in step 1) is 1:0.5 to 1.5.
3. The method according to claim 2, wherein the temperature of the one-stage low-temperature calcination in step 1) is 200 to 600 ℃ and the time of the one-stage low-temperature calcination is 0.5 to 5 hours.
4. A method according to claim 2 or 3, wherein the temperature of the two-stage pyrolysis in step 1) is 700 to 1000 ℃ and the time of the two-stage pyrolysis is 0.5 to 3 hours.
5. The method according to claim 4, wherein the concentration of the alkaline solution in step 2) is 50 to 300g/L.
6. The method according to claim 4, wherein in the step 3), the mass-to-volume ratio of the roasting material to the water is 1g: 3-15 mL.
7. The method according to claim 5 or 6, wherein the leaching in step 3) is carried out at a temperature of 30-95 ℃ for a period of 0.5-5 hours.
8. The method of claim 7, wherein the number of times of the multiple cycle leaching of step 4) is 5 to 20.
CN202310820449.1A 2023-07-05 2023-07-05 A method for efficiently separating lithium and aluminum from aluminum electrolyte waste residue and enriching lithium Pending CN116768246A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN118047401A (en) * 2024-02-18 2024-05-17 郑州大学 A method for reducing lithium content in lithium-rich electrolyte for aluminum electrolysis and recovering lithium
CN118164510A (en) * 2024-02-05 2024-06-11 郑州大学 A method for coordinated treatment and resource utilization of overhaul slag, fly ash and desulfurized gypsum

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN118164510A (en) * 2024-02-05 2024-06-11 郑州大学 A method for coordinated treatment and resource utilization of overhaul slag, fly ash and desulfurized gypsum
CN118047401A (en) * 2024-02-18 2024-05-17 郑州大学 A method for reducing lithium content in lithium-rich electrolyte for aluminum electrolysis and recovering lithium

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