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TWI428279B - Recovery of lithium from aqueous solutions - Google Patents

Recovery of lithium from aqueous solutions Download PDF

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TWI428279B
TWI428279B TW099137047A TW99137047A TWI428279B TW I428279 B TWI428279 B TW I428279B TW 099137047 A TW099137047 A TW 099137047A TW 99137047 A TW99137047 A TW 99137047A TW I428279 B TWI428279 B TW I428279B
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lithium
stream
sulfate
solution
lithium hydroxide
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TW099137047A
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TW201130738A (en
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David Buckley
J David Genders
Dan Atherton
Rainer Aul
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Rockwood Lithium Inc
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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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/10Energy storage using batteries

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Description

自水溶液中回收鋰 Recovery of lithium from aqueous solution

本發明之一部分係關於自含鋰溶液中回收鋰,該等含鋰溶液為例如製造鋰離子電池中使用之進料流以及藉由自基於礦石之材料中提取鋰而得到之進料流。 Part of the invention relates to the recovery of lithium from a lithium-containing solution which is, for example, a feed stream used in the manufacture of lithium ion batteries and a feed stream obtained by extracting lithium from an ore-based material.

本申請案主張2008年11月17日申請之美國臨時申請案第61/199,495號之權利,該案出於所有目的以全文引用的方式併入於此。 The present application claims the benefit of U.S. Provisional Application Serial No. 61/199, 495, filed on Jan. 17, 2008, which is hereby incorporated by reference.

含鋰電池,由於其具有較高能量密度重量比以及相較其他類型電池具有相對較長使用壽命,已成為多種現有及新興應用中之較佳電池。鋰離子電池用於眾多應用中,例如行動電話、膝上型電腦、醫療器件及植入物(諸如心臟起搏器)。 Lithium-containing batteries have become the preferred battery in many existing and emerging applications due to their higher energy density to weight ratio and relatively long life compared to other types of batteries. Lithium-ion batteries are used in a variety of applications, such as mobile phones, laptops, medical devices, and implants (such as cardiac pacemakers).

鋰離子電池在新型汽車(例如混合及電動車輛)的研發中亦成為極其有用之能源選擇,由於其減少排放且降低對烴燃料之依賴,故而既環保又「綠色」。此顯然為一大優勢,因為此等電池的使用消除或減少了對烴燃料之需求及所產生之溫室氣體排放,以及由於內燃引擎中化石燃料燃燒所致之其他相關環境破壞。此外,選擇鋰離子電池供車輛使用在很大程度上歸因於較高能量密度重量比,從而使得電池重量相較其他電池減輕,此為車輛製造中之重要因素。 Lithium-ion batteries are also an extremely useful energy source in the development of new types of vehicles, such as hybrid and electric vehicles. They are environmentally friendly and "green" because they reduce emissions and reduce dependence on hydrocarbon fuels. This is clearly a big advantage because the use of such batteries eliminates or reduces the need for hydrocarbon fuels and the resulting greenhouse gas emissions, as well as other related environmental damage due to fossil fuel combustion in internal combustion engines. In addition, the choice of lithium ion batteries for vehicle use is largely due to the higher energy density to weight ratio, thereby making the battery weight lighter than other batteries, which is an important factor in vehicle manufacturing.

鋰離子電池通常由三個主要部分構成:1)碳陽極,2)分 離器,及3)含鋰陰極材料。較佳含鋰陰極材料包括鋰及金屬氧化物材料,諸如鋰鈷氧化物、鋰鎳鈷氧化物、鋰錳氧化物及磷酸鋰鐵,但其他鋰化合物亦可使用。 Lithium-ion batteries usually consist of three main parts: 1) carbon anode, 2) The separator, and 3) lithium-containing cathode material. Preferred lithium-containing cathode materials include lithium and metal oxide materials such as lithium cobalt oxide, lithium nickel cobalt oxide, lithium manganese oxide, and lithium iron phosphate, but other lithium compounds may also be used.

磷酸鋰鐵為用作含鋰陰極材料之尤佳化合物,因為與所提及之其他陰極材料相比,其提供改良之安全概況、可接受之工作特徵及較低之毒性。相對較大之電池尺寸尤其如此,諸如用於電動汽車中之情況。安全特徵改良係由於磷酸鋰鐵(亦稱為LIP)能夠避免如其他鋰離子電池一般易於過熱。此對較大電池尤其重要。同時,LIP電池之電池工作特徵與目前使用之其他化合物等同。其他鋰化合物減少了過熱傾向,但以犧牲工作特徵為代價。磷酸鋰鐵硫酸鹽類似於LIP,且亦用於電池中。 Lithium iron phosphate is a particularly preferred compound for use as a lithium-containing cathode material because it provides an improved safety profile, acceptable operating characteristics, and lower toxicity compared to other cathode materials mentioned. This is especially true for relatively large battery sizes, such as those used in electric vehicles. The improvement in safety features is due to the fact that lithium iron phosphate (also known as LIP) can be easily overheated as other lithium ion batteries. This is especially important for larger batteries. At the same time, the battery operating characteristics of the LIP battery are equivalent to other compounds currently in use. Other lithium compounds reduce the tendency to overheat, but at the expense of operating characteristics. Lithium iron phosphate sulfate is similar to LIP and is also used in batteries.

磷酸鋰鐵可用濕式化學法,使用含鋰離子之水溶液進料流來製備,該等鋰離子係來自例如碳酸鋰、單水合氫氧化鋰、硝酸鋰等鋰源。典型反應流程係由Yang等人,Journal of Power Sources 146(2005)539-543描述,如下進行:3LiNO3+3Fe(NO3)2˙nH2O+3(NH4)2HPO4 → Fe3(PO4)2˙nH2O+Li3PO4+6NH3+9HNO3 (I) Lithium iron phosphate can be prepared by a wet chemical method using an aqueous solution containing lithium ions derived from a lithium source such as lithium carbonate, lithium hydroxide monohydrate or lithium nitrate. A typical reaction scheme is described by Yang et al., Journal of Power Sources 146 (2005) 539-543, as follows: 3LiNO 3 +3Fe(NO 3 ) 2 ̇ n H 2 O+3(NH 4 ) 2 HPO 4 → Fe 3 (PO 4 ) 2 ̇ n H 2 O+Li 3 PO 4 +6NH 3 +9HNO 3 (I)

Fe3(PO4)2˙nH2O+Li3PO4 → 3LiFePO4+nH2O (II) Fe 3 (PO 4 ) 2 ̇ n H 2 O+Li 3 PO 4 → 3LiFePO 4 + n H 2 O (II)

磷酸鋰鐵可用濕式化學法,使用含鋰離子之水溶液進料流來製備,該等鋰離子係來自例如碳酸鋰、單水合氫氧化鋰、硝酸鋰等鋰源。磷酸鋰鐵硫酸鹽以類似方式製備,但 製備需要硫酸鹽原料。舉例而言,Goodenough等人之美國專利第5,910,382號及Armand等人之美國專利第6,514,640號各描述磷酸鋰鐵之水溶液製備。一般而言,由於方法效率低,故此等製備磷酸鋰鐵之濕式化學法產生含有大量鋰離子以及其他雜質的水溶液流。由濕式化學法製備磷酸鋰鐵產生之典型液流的組成如下: Lithium iron phosphate can be prepared by a wet chemical method using an aqueous solution containing lithium ions derived from a lithium source such as lithium carbonate, lithium hydroxide monohydrate or lithium nitrate. Lithium iron phosphate sulfate is prepared in a similar manner, but a sulfate raw material is required for the preparation. For example, the preparation of an aqueous solution of lithium iron phosphate is described in U.S. Patent No. 5,910,382 to the name of U.S. Pat. In general, due to the low efficiency of the process, the wet chemical process for preparing lithium iron phosphate produces an aqueous solution stream containing a large amount of lithium ions and other impurities. The composition of a typical liquid stream produced by the wet chemical method for the preparation of lithium iron phosphate is as follows:

由於鋰為磷酸鋰鐵材料之主要且較有價值之組分之一,因此將需要回收任何過量鋰以在濕式化學法製造磷酸鋰鐵 中再使用,在生產磷酸鋰鐵產品之製造過程中提供相對大量過量之鋰的情況下尤其如此。自鋰電池廢料中回收並純化鋰之方法獲知於已公開之PCT申請案WO 98/59385,但此項技術中需要回收鋰之改良及替代方法。 Since lithium is one of the major and valuable components of lithium iron phosphate materials, it will be necessary to recover any excess lithium to produce lithium iron phosphate in wet chemical processes. This is especially true when used in the manufacture of lithium iron phosphate products to provide a relatively large excess of lithium. A method of recovering and purifying lithium from lithium battery waste is known from the published PCT application WO 98/59385, but there is a need in the art for improvements and alternative methods of recovering lithium.

本發明利用雙極電滲析來達成此目的及其他目的,雙極電滲析亦稱為用以自進料流中回收鋰之鹽裂解技術(salt splitting technology)。所回收之鋰呈氫氧化鋰溶液形式,可使其再循環至所用進料流中以使用濕式化學法生產磷酸鋰鐵。該過程中亦產生硫酸溶液,可將其回收並用於其他過程中或作為商品出售。在較佳實施例中,在對進料流進行雙極電滲析之前減少或更佳移除進料流中之任何磷酸根離子,因為已發現,磷酸鹽易於污染膜,從而降低氫氧化鋰之產率或完全阻止其形成。或者,在含鋰礦石之硫酸還原中,所得經純化之硫酸鋰液流亦可依此方式處理。其優勢在於亦產生硫酸液流,若加以濃縮,則可用於抵消購買所需硫酸之成本。 The present invention utilizes bipolar electrodialysis for this and other purposes, and bipolar electrodialysis is also known as a salt splitting technique for recovering lithium from a feed stream. The recovered lithium is in the form of a lithium hydroxide solution which can be recycled to the feed stream used to produce lithium iron phosphate using wet chemical methods. A sulfuric acid solution is also produced in the process which can be recovered and used in other processes or sold as a commodity. In a preferred embodiment, any phosphate ions in the feed stream are reduced or better removed prior to bipolar electrodialysis of the feed stream, as it has been found that phosphate tends to contaminate the membrane, thereby reducing lithium hydroxide. Yield or completely prevent its formation. Alternatively, in the reduction of sulfuric acid containing lithium ore, the resulting purified lithium sulfate stream can also be treated in this manner. The advantage is that a flow of sulfuric acid is also produced, which, if concentrated, can be used to offset the cost of purchasing the desired sulfuric acid.

雙極膜電滲析利用獨立腔室及膜來產生所引入之各別鹽溶液的酸及鹼。根據此方法,離子交換膜經由電場分離溶液中之離子物質。雙極膜將水解離成帶正電之氫離子(H+,在水溶液中以H3O+(水合氫離子)形式存在)及帶負電之氫氧根陰離子(OH-) Bipolar membrane electrodialysis utilizes separate chambers and membranes to produce the acid and base of the individual salt solutions introduced. According to this method, the ion exchange membrane separates the ionic species in the solution via an electric field. The bipolar membrane will hydrolyze into positively charged hydrogen ions (H + , in the form of H 3 O + (hydrated hydrogen ions) in aqueous solution) and negatively charged hydroxide anions (OH - )

雙極膜通常由結合在一起之陰離子交換層及陽離子交換層形成。提供水擴散層或界面,來自外部水性鹽溶液之水 於其中擴散。 Bipolar membranes are typically formed from an anion exchange layer and a cation exchange layer that are bonded together. Provide a water diffusion layer or interface, water from an external aqueous salt solution Spread in it.

進一步提供陰離子及陽離子可選擇性滲透之膜以引導鹽離子分離,例如必要時,鋰離子及硫酸根離子。因此,在雙極膜電滲析中通常使用三膜系統。 Further provided are anion and cation selectively permeable membranes to direct salt ion separation, such as lithium ions and sulfate ions, if desired. Therefore, a three-membrane system is commonly used in bipolar membrane electrodialysis.

來自市售來源之膜,例如Astom之ACM、CMB、AAV及BP1膜或FumaTech之FKB膜,可以其對無用離子(H+或OH-)回遷之抗性、低電阻率及對所得酸與鹼溶液之潛在腐蝕性質的抗性組合使用。此等膜定位於電極,亦即陽極與陰極之間,且電極間施加直流電(DC)。 Membranes from commercially available sources, such as Astom's ACM, CMB, AAV and BP1 membranes or FumaTech's FKB membranes, may be resistant to unwanted ions (H + or OH - ), low resistivity and the resulting acid and base The resistance to the potentially corrosive nature of the solution is used in combination. These membranes are positioned between the electrodes, that is, between the anode and the cathode, and direct current (DC) is applied between the electrodes.

較佳的池製造商包括Eurodia,且EUR20及EUR40為較佳。 Preferred cell manufacturers include Eurodia, with EUR20 and EUR40 being preferred.

使用雙極膜技術自含硫酸鋰之液流中以氫氧化鋰形式回收鋰之較佳配置展示於圖1中。如圖1所示,「A」為陰離子可滲透膜;「C」為陽離子可滲透膜。「B」為雙極膜。陰離子膜允許帶負電之硫酸根離子通過,但阻止帶正電之鋰離子通過。相反地,陽離子膜允許帶正電之鋰離子穿過,但阻止硫酸根負離子通過。圖中間展示預帶電之酸與鹼儲集器,所得H+或OH-離子與所析出之帶負電之硫酸根離子及帶正電之鋰離子組合。因此,產生氫氧化鋰溶液,可將其饋入製備磷酸鋰鐵之過程液流中。在陰極側得到硫酸溶液。 A preferred configuration for recovering lithium in the form of lithium hydroxide from a liquid stream containing lithium sulfate using a bipolar membrane technique is shown in FIG. As shown in Fig. 1, "A" is an anion permeable membrane; "C" is a cationic permeable membrane. "B" is a bipolar membrane. The anionic membrane allows the passage of negatively charged sulfate ions, but prevents the passage of positively charged lithium ions. Conversely, the cation membrane allows positively charged lithium ions to pass through, but prevents the passage of sulfate anions. The pre-charged acid and alkali reservoir is shown in the middle of the figure, and the resulting H + or OH - ions are combined with the precipitated negatively charged sulfate ions and positively charged lithium ions. Thus, a lithium hydroxide solution is produced which can be fed into the process stream for the preparation of lithium iron phosphate. A sulfuric acid solution was obtained on the cathode side.

較佳的是,藉由添加適合之鹼,較佳為鹼金屬氫氧化物,對先前所述類型之硫酸鋰溶液進行預處理,達到相對較高pH值,通常達到10至11之pH值。氫氧化鋰、氫氧化 鈉、氫氧化鉀尤佳。將pH值調整至此範圍可移除雜質,如沈澱物,尤其係可能干擾電滲析裝置中之電化學反應的磷酸鹽。尤佳的是,至少自進料中移除磷酸鹽,因為已發現,此雜質尤其會導致膜受污染,從而破壞過程進行。在饋入雙極電滲析池中之前,自溶液中過濾此等沈澱物。接著視需要可將溶液調整至較低pH值,例如pH 1-4,且較佳為2-3,較佳係利用自過程中得到之酸來作調整,接著將溶液饋入電滲析池中。如上所述,在此過程中,鋰離子穿過陽離子膜,產生氫氧化鋰液流;且硫酸根穿過陰離子膜,產生硫酸液流。(見圖1) Preferably, the lithium sulphate solution of the type previously described is pretreated by the addition of a suitable base, preferably an alkali metal hydroxide, to a relatively high pH, typically to a pH of from 10 to 11. Lithium hydroxide, hydrogen hydroxide Sodium and potassium hydroxide are especially preferred. Adjusting the pH to this range removes impurities, such as precipitates, especially phosphates that may interfere with the electrochemical reactions in the electrodialysis unit. It is especially preferred to remove the phosphate from at least the feed, as it has been found that this impurity particularly causes the membrane to become contaminated, thereby disrupting the process. These precipitates were filtered from the solution before being fed into the bipolar electrodialysis cell. The solution can then be adjusted to a lower pH, such as pH 1-4, and preferably 2-3, as desired, preferably by adjustment from the acid obtained in the process, followed by feeding the solution into the electrodialysis cell. As described above, in this process, lithium ions pass through the cation membrane to produce a lithium hydroxide stream; and the sulfate passes through the anion membrane to produce a sulfuric acid stream. (see picture 1)

所得LiOH及硫酸液流就各別組分之莫耳含量而言為相對較弱之液流。舉例而言,測試展示如下平均範圍:LiOH:1.6-1.85M H2SO4:0.57-1.1M The resulting LiOH and sulfuric acid streams are relatively weak streams for the molar content of the individual components. For example, the test shows the following average range: LiOH: 1.6-1.85MH 2 SO 4 : 0.57-1.1M

本發明之另一態樣係關於氫氧化鋰產物之純度,因為經純化之氫氧化鋰產物為極其需要的。 Another aspect of the invention pertains to the purity of the lithium hydroxide product, as the purified lithium hydroxide product is highly desirable.

已發現,硫酸產物濃度降低約50%使得氫氧化物溶液中之硫酸根濃度下降相應的量(自430ppm至200ppm)。另外,隨著酸濃度降低,相對於酸產生之電流效率增加約10%。 It has been found that a reduction in the sulfuric acid product concentration of about 50% causes the sulfate concentration in the hydroxide solution to decrease by a corresponding amount (from 430 ppm to 200 ppm). In addition, as the acid concentration decreases, the current efficiency relative to the acid generation increases by about 10%.

上述過程之方塊圖展示於圖2中。 A block diagram of the above process is shown in FIG.

更特定言之,參考圖2,藉由將pH值調整至約10至約11以使任何固體雜質自進料流中沈澱出,從而移除任何固體雜質來純化含硫酸鋰之進料流,較佳為來自鋰電池組分生產中之進料流。接著對所得經純化之硫酸鋰進料流進行雙 極滲析,滲析前較佳用硫酸將pH值調整至約2-3.5,使用適合之雙極膜以自液流中分離鋰,其將以氫氧化鋰形式回收。在一個較佳實施例中,在對硫酸鋰進料流進行雙極電滲析之前,在純化步驟之前或可能在純化步驟期間,藉由例如調整pH值以移除磷酸鹽或藉由使用適當離子交換膜以自溶液中移除磷酸鹽,藉此移除任何磷酸鹽。或者,來自硫酸礦石提取過程之硫酸鋰液流,已按此項技術中已知之慣例適當純化,可對之進行雙極滲析,滲析前較佳用硫酸將pH值調整至約2-3.5,使用適合之雙極膜以自液流中分離鋰,其將以氫氧化鋰形式回收。 More specifically, referring to Figure 2, the lithium sulfate-containing feed stream is purified by adjusting the pH to from about 10 to about 11 to precipitate any solid impurities from the feed stream, thereby removing any solid impurities. It is preferably a feed stream from the production of lithium battery components. The resulting purified lithium sulfate feed stream is then doubled Extremely dialysis, preferably prior to dialysis, the pH is adjusted to about 2-3.5 with sulfuric acid, using a suitable bipolar membrane to separate lithium from the liquid stream, which will be recovered as lithium hydroxide. In a preferred embodiment, prior to the bipolar electrodialysis of the lithium sulfate feed stream, prior to the purification step or possibly during the purification step, for example, by adjusting the pH to remove phosphate or by using appropriate ions The membrane is exchanged to remove phosphate from the solution, thereby removing any phosphate. Alternatively, the lithium sulphate stream from the sulphate ore extraction process has been suitably purified according to the practices known in the art, which can be subjected to bipolar dialysis. Preferably, the pH is adjusted to about 2-3.5 with sulphuric acid prior to dialysis. Suitable bipolar membranes separate lithium from the liquid stream, which will be recovered as lithium hydroxide.

據信,電流效率低,尤其當其涉及陽離子膜時,會導致鄰近膜之局部pH值較高,從而在中央進料室中形成沈澱物。亦可在池外部,藉由有意將進料之pH值升至10且允許形成沈澱物而觀察到此情況。表1展示自pH值已調整至10,靜置隔夜並過濾之硫酸鋰進料溶液之10L批料中收集之固體的組成。總計回收到3.02g固體。將一部分固體(0.3035g)再溶解於100ml之1M HCl中,以由ICP2分析。自下表1可見,沈澱物中之主要雜質似為Fe、Cu、P、Si、Zn及Mn3。 It is believed that current efficiency is low, especially when it involves a cationic membrane, which results in a higher local pH of the adjacent membrane, thereby forming a precipitate in the central feed chamber. This can also be observed outside the cell by intentionally raising the pH of the feed to 10 and allowing the formation of a precipitate. Table 1 shows the composition of the solids collected from the 10 L batch of the lithium sulfate feed solution that had been adjusted to pH 10 and allowed to stand overnight and filtered. A total of 3.02 g of solid was recovered. A portion of the solid (0.3035 g) was redissolved in 100 mL of 1 M HCl for analysis by ICP. As can be seen from Table 1 below, the main impurities in the precipitate appear to be Fe, Cu, P, Si, Zn and Mn3.

用適合之雙極膜對硫酸鋰進料流進行雙極滲析得到氫氧化鋰溶液及硫酸溶液,分別如圖2右側及左側所示。 The lithium hydroxide solution and the sulfuric acid solution were obtained by bipolar dialysis of the lithium sulfate feed stream with a suitable bipolar membrane, as shown in the right side and the left side of Fig. 2, respectively.

可回收氫氧化鋰溶液,或較佳可將其直接引入製備LiFePO4或其他含鋰鹽或產物之過程中。當然,可回收氫氧化鋰,且將其用作例如適合化學反應中之鹼或用於調整初始進料流之pH值以移除諸如磷酸鹽之雜質。 The lithium hydroxide solution can be recovered, or preferably it can be directly introduced into the process of preparing LiFePO 4 or other lithium-containing salts or products. Of course, lithium hydroxide can be recovered and used, for example, as a base suitable for chemical reactions or to adjust the pH of the initial feed stream to remove impurities such as phosphate.

視需要可在使用前濃縮所回收之氫氧化鋰溶液,或在必要時對其進行其他純化步驟。 The recovered lithium hydroxide solution may be concentrated before use, or may be subjected to other purification steps as necessary.

現轉向圖2左側,回收硫酸溶液並出售,或將其用作適合化學及工業過程中之酸。或者,可將其濃縮,且用於抵消購買自含鋰礦石中以酸提取鋰所需之硫酸的相關成本。 Turning now to the left side of Figure 2, the sulfuric acid solution is recovered and sold, or used as an acid suitable for chemical and industrial processes. Alternatively, it can be concentrated and used to offset the associated costs of purchasing the sulfuric acid required to extract lithium from the lithium-containing ore.

圖3展示本發明之一個替代實施例,其中氫氧化鋰與硫 酸液流均被回收且用於製造磷酸鋰鐵之過程中,此基本上使該過程連續進行。由於在該過程中鐵以硫酸鐵之形式添加,故使用所回收之硫酸液流形成硫酸鐵為可行的。此將取決於硫酸鐵之純度需求以及所需之濃度水準。然而,根據此方法,可利用替代硫酸鐵之鐵源以及提供硫酸根來源之硫酸溶液。 Figure 3 shows an alternative embodiment of the invention in which lithium hydroxide and sulfur The acid stream is recovered and used in the manufacture of lithium iron phosphate, which essentially allows the process to proceed continuously. Since iron is added in the form of ferric sulfate in the process, it is feasible to form the ferric sulfate using the recovered sulfuric acid stream. This will depend on the purity requirements of the ferric sulphate and the level of concentration required. However, according to this method, an alternative source of iron for ferric sulfate and a solution of sulfuric acid derived from a sulfate source can be utilized.

更特定言之,在圖3中,如上所述,在進行電滲析之前藉由將pH值調整至10-11,接著將pH值下調至2-3.5來純化硫酸鋰進料流。 More specifically, in Figure 3, the lithium sulfate feed stream was purified prior to electrodialysis by adjusting the pH to 10-11, followed by downregulating the pH to 2-3.5, as described above.

如同圖2,用適合之膜對純化流進行雙極電滲析以形成硫酸水溶液流及氫氧化鋰水溶液進料流。在此實施例中,重點在於回收硫酸與氫氧化鋰進料流且使之返回用於鋰產品,尤其磷酸鋰鐵的生產中。現關注於圖3左側,藉由向硫酸溶液中添加鐵源而使硫酸水溶液流轉化成硫酸鐵。鐵源可為任何合適之來源,包括天然存在之鐵礦石中所見之金屬鐵。由於硫酸鐵溶液已含有硫酸根離子,故硫酸鐵為較佳鐵鹽。添加鐵得到磷酸鐵溶液,接著使該磷酸鐵溶液最終與自雙極電滲析過程中回收之氫氧化鋰溶液以及磷酸鹽原料混合以得到磷酸鋰鐵。 As in Figure 2, the purified stream was subjected to bipolar electrodialysis using a suitable membrane to form an aqueous solution of aqueous sulfuric acid and a feed stream of aqueous lithium hydroxide solution. In this embodiment, the focus is on recovering the sulfuric acid and lithium hydroxide feed streams and returning them for use in the production of lithium products, particularly lithium iron phosphate. Focusing now on the left side of Figure 3, the aqueous sulfuric acid stream is converted to ferric sulfate by the addition of an iron source to the sulfuric acid solution. The iron source can be of any suitable source, including metallic iron as seen in naturally occurring iron ore. Since the ferric sulfate solution already contains sulfate ions, ferric sulfate is a preferred iron salt. Iron is added to obtain an iron phosphate solution, and then the iron phosphate solution is finally mixed with a lithium hydroxide solution recovered from the bipolar electrodialysis process and a phosphate raw material to obtain lithium iron phosphate.

如圖3右側所示,較佳藉由自另一來源引入氫氧化鋰或藉由濃縮所回收之液流,將氫氧化鋰溶液調整至所需氫氧化鋰含量。 As shown on the right side of Figure 3, the lithium hydroxide solution is preferably adjusted to the desired lithium hydroxide content by introducing lithium hydroxide from another source or by concentrating the recovered stream.

另一較佳實施例展示於圖4中。在此選擇方案中,過程中使用非氫氧化鋰之鋰源,例如碳酸鋰。在此實施例中, 使硫酸液流與預定純度之碳酸鋰反應,以產生額外硫酸鋰溶液,接著將其添加至原始再循環溶液中,隨後饋入雙極電滲析池中。此過程展示於圖4中之流程圖左側。因此,可使用不同鋰源來得到可提取出氫氧化鋰之鋰溶液。LiSO4進料流之pH值調整步驟如上所述。 Another preferred embodiment is shown in FIG. In this alternative, a lithium source other than lithium hydroxide, such as lithium carbonate, is used in the process. In this embodiment, the sulfuric acid stream is reacted with lithium carbonate of a predetermined purity to produce an additional lithium sulfate solution, which is then added to the original recycle solution and subsequently fed to the bipolar electrodialysis cell. This process is shown on the left side of the flow chart in Figure 4. Therefore, different lithium sources can be used to obtain a lithium solution in which lithium hydroxide can be extracted. The pH adjustment step of the LiSO 4 feed stream is as described above.

注意,根據諸如本文所述之濕式化學法,展示將硫酸鐵添加至全部或一部分硫酸液流中以得到硫酸鐵溶液,其與所回收之氫氧化鋰溶液一起用於產生磷酸鋰鐵。 Note that according to a wet chemical process such as described herein, it is shown that iron sulphate is added to all or a portion of the sulphuric acid stream to obtain an iron sulphate solution for use with the recovered lithium hydroxide solution to produce lithium iron phosphate.

實例1Example 1

對購自Euroduce之EUR-2C電滲析池進行改進,使其包括Astom雙極膜(BP1)以及FuMaTech陰離子及陽離子膜(分別為FAB及FKB)。向該池中通入經預處理而將pH值調整至10之進料溶液以使磷酸鹽及其他雜質沈澱出,繼而過濾以移除沈澱物。接著將pH值調整至pH 3.5,隨後饋入池中。 The EUR-2C electrodialysis cell purchased from Euroduce was modified to include Astom bipolar membrane (BP1) and FuMaTech anion and cationic membranes (FAB and FKB, respectively). A feed solution pretreated to adjust the pH to 10 was introduced into the cell to precipitate phosphate and other impurities, which were then filtered to remove the precipitate. The pH was then adjusted to pH 3.5 and then fed into the cell.

自表2可見,電流效率為約75%時,陽離子膜產生至多2.16M LiOH。電流效率為40%時,陰離子交換膜產生0.6M H2SO4產物溶液。在整個操作中平均電流密度接近於62mA/cm2,同時該池在25V之恆定電壓下工作(此電壓施加於全部七組膜及電極沖洗室之間)。在此短期工作下,池中未觀察到固體,此表明向池中引入進料溶液之前,藉由預處理將pH值調整至10,與未調整pH值之進料溶液相比,結果得到改良。 It can be seen from Table 2 that the cation membrane produces up to 2.16 M LiOH at a current efficiency of about 75%. At a current efficiency of 40%, the anion exchange membrane produced a 0.6 MH 2 SO 4 product solution. The average current density was close to 62 mA/cm 2 throughout the operation while the cell was operated at a constant voltage of 25 V (this voltage was applied between all seven sets of membranes and the electrode wash chamber). Under this short-term work, no solids were observed in the pool, indicating that the pH was adjusted to 10 by pretreatment before introducing the feed solution into the tank, and the results were improved compared to the unadjusted feed solution. .

由於吾人須使用一種產物流以維持中央室中之pH值,因 此池之總效率似乎由任何特定膜之最低電流效率決定。因此,在實例1中有必要將一些產物LiOH回添至中央室中,以中和自酸室回遷之質子。因此,池之總電流效率應為40%,消除了FKB膜之優勢。 Since we have to use a product stream to maintain the pH in the central chamber, The overall efficiency of this cell appears to be determined by the lowest current efficiency of any particular membrane. Therefore, in Example 1, it is necessary to add some of the product LiOH back to the central chamber to neutralize the protons relocated from the acid chamber. Therefore, the total current efficiency of the cell should be 40%, eliminating the advantages of the FKB film.

實例2-5Example 2-5

實例2至5皆使用Astom膜(ACM、CMB及BPI)來操作。實例2及3為短期實驗,其使用如前所述經預處理至pH 10的硫酸鋰進料溶液。兩個實例均得到接近於60%之酸及鹼電流效率,且在短期內維持良好的電流密度,此表明預處理與先前操作相比,結果得到改良。實例4為隔夜實驗,其使用相同條件來操作,且顯示電流密度顯著下降,此可能由於膜受到磷酸鹽或其他沈澱物的污染。 Examples 2 through 5 were all operated using Astom membranes (ACM, CMB and BPI). Examples 2 and 3 are short-term experiments using a lithium sulfate feed solution pretreated to pH 10 as previously described. Both examples obtained acid and alkali current efficiencies close to 60% and maintained good current densities in the short term, indicating that the pretreatment was improved compared to previous operations. Example 4 is an overnight experiment that operates using the same conditions and shows a significant decrease in current density, which may be due to contamination of the membrane with phosphate or other deposits.

圖5展示全部三個操作之電流密度。1250分鐘後,暫停池並關閉泵以便上樣。在重啟系統時,電流密度明顯恢復,此表明電流下降係由於少量沈澱物,隨後將其自池中洗去。 Figure 5 shows the current densities of all three operations. After 1250 minutes, pause the pool and turn off the pump to load. When the system was restarted, the current density recovered significantly, indicating that the current drop was due to a small amount of precipitate which was subsequently washed away from the cell.

由於預處理至pH 10可能使一些污染物殘留於進料流中,故實例5使用經預處理至pH 11並維持3天,接著加以過濾之溶液。如圖6所示,電流密度維持24小時以上,結果得到明顯改良。電流最終下降據信係由於進料中之硫酸鋰逐漸耗盡,此硫酸鋰以單一大批量操作。 Since pretreatment to pH 10 may cause some contaminants to remain in the feed stream, Example 5 used a solution that was pretreated to pH 11 and maintained for 3 days, followed by filtration. As shown in Fig. 6, the current density was maintained for more than 24 hours, and the result was remarkably improved. The final drop in current is believed to be due to the gradual depletion of lithium sulfate in the feed, which is operated in a single large batch.

圖6亦顯示,藉由恆定地添加水,使酸及鹼之濃度維持相當恆定。因此,需要且有時有必要添加產物酸或鹼以控制中央進料室中之pH值。為有助於控制此室,選擇較高酸 濃度,從而降低酸電流效率,使得僅藉由添加LiOH,可將中央室中之pH值控制在3.5。形成氫氧化物之平均電流密度為60%左右。 Figure 6 also shows that the concentration of acid and base is maintained fairly constant by constant addition of water. Therefore, it is necessary and sometimes necessary to add a product acid or base to control the pH in the central feed chamber. To help control this room, choose a higher acid The concentration, thereby reducing the acid current efficiency, allows the pH in the central chamber to be controlled to 3.5 only by the addition of LiOH. The average current density of the hydroxide formed is about 60%.

圖6顯示,全部三個室中之硫酸根濃度皆隨時間變化。中央室係以單一批量操作,且實驗結束時,濃度達到約0.2M。LiOH中之硫酸根為約400mg/L,佔電流的約0.85%。降低硫酸濃度會使LiOH中之硫酸根含量進一步下降。 Figure 6 shows that the sulfate concentrations in all three chambers vary with time. The central chamber was operated in a single batch and at the end of the experiment, the concentration reached approximately 0.2M. The sulfate in LiOH is about 400 mg/L, which accounts for about 0.85% of the current. Lowering the sulfuric acid concentration further reduces the sulfate content in LiOH.

實例6-10Example 6-10

在實例6-10中,使用Eurodia EUR-2C電滲析池來展示硫酸鋰之三室鹽裂解的可行性。該池裝配有七組陽離子、陰離子及雙極膜,如圖1所示進行組態。各膜之有效面積為0.02m2In Examples 6-10, the Eurodia EUR-2C electrodialysis cell was used to demonstrate the feasibility of three-chamber salt cracking of lithium sulfate. The cell is equipped with seven sets of cation, anion and bipolar membranes, configured as shown in Figure 1. The effective area of each film was 0.02 m 2 .

咸信,由於氫氧根離子回遷,在鄰近陽離子膜之高pH值區域中形成之磷酸鋰若出現,則為導致膜污染的主要原因。與將pH值僅調整至10相比,藉由將pH值升至11對進料溶液進行預處理以移除磷酸鹽及其他雜質,使得此等鹽大部分沈澱出,且得到改良結果。 It is believed that due to the reversion of hydroxide ions, lithium phosphate formed in the high pH region adjacent to the cation membrane is the main cause of membrane fouling. The phosphate solution and other impurities were removed by pretreatment of the feed solution by raising the pH to 11 to adjust the pH to only 10, so that most of the salts precipitated and improved results were obtained.

實例9為代表性實例且詳細描述如下。藉由用4M LiOH將pH值升至11來對1M硫酸鋰起始溶液進行預處理以移除不溶性磷酸鹽,比率為約1L LiOH對60L 1M Li2SO4。充分混合經處理之硫酸鋰,且使沈澱物沈降隔夜,隨後經玻璃纖維濾紙(1μm孔徑)過濾。藉由每公升Li2SO4添加約12mL 4M硫酸,將經過濾之Li2SO4的pH值再調整至pH 2。 Example 9 is a representative example and is described in detail below. The 1 M lithium sulfate starting solution was pretreated to remove insoluble phosphate by raising the pH to 11 with 4M LiOH in a ratio of about 1 L LiOH to 60 L 1 M Li 2 SO 4 . The treated lithium sulfate was thoroughly mixed, and the precipitate was allowed to settle overnight, followed by filtration through a glass fiber filter paper (1 μm pore size). The pH of the filtered Li 2 SO 4 was adjusted to pH 2 by adding about 12 mL of 4 M sulfuric acid per liter of Li 2 SO 4 .

經預處理之Li2SO4進料的起始體積為8L,且預熱至約60℃,隨後轉移至20L玻璃進料儲集器中。初始LiOH鹼為來自實例8之3公升渣滓(heel),在實驗開始時分析得到LiOH為1.8M。初始酸為亦來自實例8之2L H2SO4渣滓,且分析得到H2SO4為0.93M。電極洗液為2公升50mM硫酸。將溶液以約0.5L/小室(總流量為3-4L/min)泵入Eurodia池(EUR-2C-BP7),各室上維持相等的反向壓力(3-4psi)以防止任一膜上之壓力過大而導致內部洩漏。監測各室之流速及壓力,以及進料溫度、進料pH值、電流、電壓、通過之電荷及進料體積。 The pretreated Li 2 SO 4 feed had a starting volume of 8 L and was preheated to about 60 ° C and subsequently transferred to a 20 L glass feed reservoir. The initial LiOH base was 3 liters of heel from Example 8, which was analyzed to give a LiOH of 1.8 M at the beginning of the experiment. The initial acid from Example 8 is also the dross 2L H 2 SO 4, and H 2 SO 4 to give analysis was 0.93M. The electrode wash was 2 liters of 50 mM sulfuric acid. The solution was pumped into the Eurodia pool (EUR-2C-BP7) at approximately 0.5 L/well (total flow rate 3-4 L/min), maintaining equal back pressure (3-4 psi) on each chamber to prevent either membrane The pressure is too large and causes internal leakage. The flow rate and pressure of each chamber were monitored, as well as feed temperature, feed pH, current, voltage, charge passed, and feed volume.

電滲析於25伏恆定電壓下進行。Li2SO4進料溫度控制在35℃。泵(TE-MDK-MT3,Kynar March Pump)及ED池提供足夠熱量來維持溫度。給20公升進料罐加上護套,使得當溫度超過35℃時,冷卻水可經由螺線管閥門及溫度控制器(OMEGA CN76000)泵入護套。 Electrodialysis was carried out at a constant voltage of 25 volts. The Li 2 SO 4 feed temperature was controlled at 35 °C. The pump (TE-MDK-MT3, Kynar March Pump) and the ED pool provide enough heat to maintain the temperature. A 20 liter feed tank is jacketed so that when the temperature exceeds 35 ° C, the cooling water can be pumped into the jacket via a solenoid valve and temperature controller (OMEGA CN76000).

池膜提供充足熱傳遞以冷卻其他室。為使此實驗連續進行20小時,泵送補充經預處理至pH 2之Li2SO4進料,1M Li2SO4進料之連續速率為10mL/min。穿過ACM膜回遷之質子多於穿過FKB陽離子膜回遷之氫氧根,因此,中央室之pH值通常會下降。藉由使用高鈉pH值之電極及設定於pH 2之JENCO pH/ORP控制器添加4M LiOH來控制中央室的pH值。在20小時實驗中每分鐘進料pH值之電子數據記錄顯示pH值之變化範圍為1.9至2.1,因此,總計3.67L之4M LiOH添加至進料中以中和氫氧根回遷。操作進行20小 時之後,由於添加11.8L Li2SO4及3.7L LiOH以及向酸中輸送6.8L水並向鹼中輸送0.7L水,進料體積自8L增至15.3L。 The cell membrane provides sufficient heat transfer to cool other chambers. To allow this experiment to run continuously for 20 hours, the Li 2 SO 4 feed pretreated to pH 2 was pumped and the continuous rate of 1 M Li 2 SO 4 feed was 10 mL/min. The protons that migrate through the ACM membrane are more than the hydroxides that migrate back through the FKB cation membrane, so the pH of the central compartment usually decreases. The pH of the central chamber was controlled by the addition of 4M LiOH using a high sodium pH electrode and a JENCO pH/ORP controller set at pH 2. An electronic data record of the feed pH per minute during the 20 hour experiment showed a pH ranging from 1.9 to 2.1, so a total of 3.67 L of 4 M LiOH was added to the feed to neutralize the hydroxide reversion. After 20 hours of operation, the feed volume increased from 8 L to 15.3 L due to the addition of 11.8 L Li 2 SO 4 and 3.7 L LiOH and the transport of 6.8 L of water to the acid and 0.7 L of water to the base.

LiOH鹼自1加侖封閉聚丙烯罐循環流經池。藉由使用固定於LiOH表面之管自頂部排放而維持3公升體積,且使用蠕動泵將LiOH產物收集於15加侖溢出容器(overflow container)中。藉由向LiOH罐中以17mL/min之恆定速率添加水,使LiOH濃度維持於1.85M LiOH濃度。 LiOH base is circulated through the cell from a 1 gallon closed polypropylene tank. The 3 liter volume was maintained by draining from the top using a tube fixed to the LiOH surface, and the LiOH product was collected in a 15 gallon overflow container using a peristaltic pump. The LiOH concentration was maintained at a concentration of 1.85 M LiOH by adding water to the LiOH tank at a constant rate of 17 mL/min.

硫酸自2L玻璃儲集器循環流經池之酸室。接近儲集器頂部之溢出口維持2.2L H2SO4之恆定體積,溢出之酸產物流入15加侖罐中。藉由以16mL/min之恆定速率添加水,使H2SO4濃度恆定地保持於1.9M。 Sulfuric acid is circulated through the acid chamber of the cell from a 2 L glass reservoir. The overflow port near the top of the reservoir maintains a constant volume of 2.2 LH 2 SO 4 and the overflowed acid product flows into the 15 gallon tank. The H 2 SO 4 concentration was kept constant at 1.9 M by adding water at a constant rate of 16 mL/min.

電極洗液(50mM H2SO4)循環流經陽極液與陰極液末端室且在2公升聚丙烯罐頂部於池出口處重新組合,其中在電極處產生之O2及H2氣體流向通風櫥後部。 An electrode wash (50 mM H 2 SO 4 ) is circulated through the anolyte and catholyte end chambers and recombined at the top of the 2 liter polypropylene can at the cell outlet, where the O 2 and H 2 gases generated at the electrodes flow to the fume hood rear.

在實驗期間採集數個樣品,以確保水添加至酸及鹼中之速率足以保持實驗過程中濃度恆定。在19.9小時實驗結束時,關閉電源,使罐排空,且量測最終產物以及最終Li2SO4及電極洗液的體積。得到總計30.1L 1.86M LiOH(包括3L渣滓)及21.1L 1.92M H2SO4(包括2L渣滓)。最終進料為15.3公升0.28M Li2SO4,且最終電極洗液含有1.5L 67mM H2SO4。電極洗液中之0.5L水穿過陽離子膜輸送至酸中。向酸及鹼中添加之水的總量分別為18.6公升及20.4公升。通過之總電荷為975660庫侖(70.78莫耳),其中33.8 莫耳H回遷,20.2莫耳OH-回遷,且14.97莫耳LiOH添加至進料中。此實驗之平均電流密度為67.8mA/cm2。基於對酸中富集之硫酸根進行分析,H2SO4電流效率為52.5%;基於對LiOH產物中之Li+進行分析,LiOH電流效率為72.4%。 Several samples were taken during the experiment to ensure that the rate of water addition to the acid and base was sufficient to maintain a constant concentration during the experiment. At the end of the 19.9 hour experiment, the power was turned off, the can was emptied, and the final product and the final volume of Li 2 SO 4 and electrode wash were measured. A total of 30.1 L of 1.86 M LiOH (including 3 L of slag) and 21.1 L of 1.92 MH 2 SO 4 (including 2 L of slag) were obtained. The final feed was 15.3 liters of 0.28 M Li 2 SO 4 and the final electrode wash contained 1.5 L of 67 mM H 2 SO 4 . 0.5 L of water in the electrode wash was passed through the cation membrane to the acid. The total amount of water added to the acid and alkali was 18.6 liters and 20.4 liters, respectively. The total charge passed was 975,660 coulombs (70.78 moles), of which 33.8 moles H relocated, 20.2 moles of OH - rebound, and 14.97 moles of LiOH were added to the feed. The average current density of this experiment was 67.8 mA/cm 2 . Based on the analysis of the sulfate enriched in the acid, the H 2 SO 4 current efficiency was 52.5%; based on the analysis of Li + in the LiOH product, the LiOH current efficiency was 72.4%.

藉由使用配備有GP50梯度泵、AS 17分析柱、ASRS300陰離子抑制器、CD25電導率偵測器、EG40 KOH溶離劑發生器及AS40自動上樣儀的Dionex DX600來分析起始樣品及最終樣品中之SO4 2-。將25μL樣品注射至分離柱上,在該分離柱中,使用1mM至30mM KOH之濃度梯度,5mM/min梯度上升,以1.5mL/min對陰離子進行溶離。藉由使用電導率偵測所產生之峰面積相對於四點校準曲線來測定硫酸根濃度,其處於2至200mg/L SO4 2-之範圍內。藉由類似技術,使用配備有IC25A等度泵、CS12a分析柱、CSRS300陽離子抑制器、IC25電導率偵測器、ECG II MSA溶離劑發生器及AS40自動上樣儀的Dionex DX320 IC來分析樣品中之Li+。將25μL樣品注射至分離柱上,在該分離柱中,使用20mM至30mM甲烷磺酸(MSA)之濃度梯度,以1.0mL/min對陰離子進行溶離。藉由使用電導率偵測所產生之峰面積相對於四點校準曲線來測定鋰濃度,其處於10至200mg/L Li+之範圍內。藉由用標準1.0N氫氧化鈉將pH值滴定至pH 7來測定H2SO4之酸濃度。藉由使用微滴管(microburrete),用標準0.50N硫酸滴定至pH 7來測定鹼濃度。 Analysis of the starting and final samples by using a Dionex DX600 equipped with a GP50 gradient pump, AS 17 analytical column, ASRS300 anion suppressor, CD25 conductivity detector, EG40 KOH eliminator and AS40 autosampler SO 4 2- . 25 μL of the sample was injected onto a separation column in which a concentration gradient of 1 mM to 30 mM KOH was used, and a gradient of 5 mM/min was raised to dissolve the anion at 1.5 mL/min. The sulfate concentration is determined by using a peak area generated by conductivity detection relative to a four-point calibration curve, which is in the range of 2 to 200 mg/L SO 4 2- . The sample was analyzed by a similar technique using a Dionex DX320 IC equipped with an IC25A isocratic pump, CS12a analytical column, CSRS300 cation suppressor, IC25 conductivity detector, ECG II MSA eliminator and AS40 autosampler. Li + . 25 μL of the sample was injected onto a separation column in which the anion was eluted at a concentration gradient of 20 mM to 30 mM methanesulfonic acid (MSA) at 1.0 mL/min. The lithium concentration is determined by using a peak area generated by conductivity detection with respect to a four-point calibration curve, which is in the range of 10 to 200 mg/L Li + . The acid concentration of H 2 SO 4 was determined by titrating the pH to pH 7 with standard 1.0 N sodium hydroxide. The alkali concentration was determined by titration with a standard 0.50 N sulfuric acid to pH 7 using a microburrete.

表3概述以Astom ACM膜進行之電滲析實驗的結果。實例6亦分別使用Astom CMB陽離子膜及BP1雙極膜。將硫酸鋰進料溶液預處理至pH 11,過濾,接著再調整至pH 3.5,隨後通入池中。有關電流效率之結果與上月報告之結果相當;然而,平均電流密度低於先前操作之電流密度,此表明仍有一些污染。陽離子膜之pH梯度在pH值為3.5時似乎引起沈澱問題,將進料室之pH值降至pH 2,且使用具有較少氫氧根回遷之FuMaTech FKB陽離子膜。FI(13與ACM膜)配對意謂中央室中之pH值係由質子穿過ACM之回遷來決定,且僅藉由添加LiOH來控制pH值。 Table 3 summarizes the results of electrodialysis experiments performed on Astom ACM membranes. Example 6 also used Astom CMB cation membrane and BP1 bipolar membrane, respectively. The lithium sulfate feed solution was pretreated to pH 11, filtered, and then adjusted to pH 3.5, and then passed to the cell. The results for current efficiency are comparable to those reported last month; however, the average current density is lower than the current operating current density, indicating some contamination. The pH gradient of the cationic membrane appeared to cause precipitation problems at pH 3.5, the pH of the feed compartment was lowered to pH 2, and a FuMaTech FKB cation membrane with less hydroxide reversion was used. The FI (13 and ACM film) pairing means that the pH in the central chamber is determined by the relocation of protons through the ACM, and the pH is controlled only by the addition of LiOH.

實例7至9使用FKB/ACM/BP1組合進行重複操作,三個批次總計進行70小時。自表3可見,此等操作之再現性極佳,以三種不同方式量測之LiOH電流效率為71-75%(由進料中Li+之損失、鹼室中Li+及氫氧根離子之增加來量測)。同樣地,由全部三種測量方法量測之酸電流效率為50-52%。此等實例之數據顯示平均電流密度的一致性。圖7圖解展示此情況,其中初始電流密度彼此匹配極好。因批次大小不同而導致各批次結束時有偏差,因此,最終硫酸鋰濃度不同。 Examples 7 through 9 were repeated using the FKB/ACM/BP1 combination, and the three batches were totaled for 70 hours. As can be seen from Table 3, the reproducibility of these operations is excellent, and the LiOH current efficiency measured in three different ways is 71-75% (loss of Li + in the feed, Li + and hydroxide ions in the alkali chamber) Increase to measure). Similarly, the acid current efficiency measured by all three measurement methods is 50-52%. The data for these examples shows the consistency of the average current density. Figure 7 illustrates this situation where the initial current densities match each other very well. Due to the difference in batch size, there is a deviation at the end of each batch, so the final lithium sulfate concentration is different.

FKB膜之高電流效率似乎有助於避免陽離子膜之進料側的邊界層處發生沈澱問題。過程之總電流效率係由表現最差之膜決定。亦即,ACM膜之低效率必須藉由將鹼室中之LiOH回添至進料室中來補償,因而總效率因陰離子膜而 降低。為增加陰離子膜之效率,降低產物酸室中之酸濃度。實例10使用0.61M硫酸進行操作,其使得酸電流效率增加了10%至62%左右。(見表3) The high current efficiency of the FKB film appears to help avoid precipitation problems at the boundary layer on the feed side of the cation membrane. The total current efficiency of the process is determined by the worst performing film. That is, the inefficiency of the ACM film must be compensated by adding the LiOH in the alkali chamber back to the feed chamber, so the overall efficiency is due to the anion membrane. reduce. To increase the efficiency of the anion membrane, the acid concentration in the acid compartment of the product is reduced. Example 10 was operated using 0.61 M sulfuric acid which increased the acid current efficiency by about 10% to about 62%. (See Table 3)

實例11-12Example 11-12

為進一步增加酸電流效率,在實例11及12中,用來自Astom之AAV替代性陰離子膜對池進行改進。AAV膜為原先可購自Ashahi Chemical之酸阻斷膜。表4展示使用FKB、AAV及BP-1雙極膜之組合進行此等實驗之數據概述。 To further increase the acid current efficiency, in Examples 11 and 12, the cell was modified with an AAV replacement anion membrane from Astom. The AAV film is an acid blocking film originally available from Ashahi Chemical. Table 4 shows an overview of the data for conducting such experiments using a combination of FKB, AAV, and BP-1 bipolar membranes.

此等膜之酸與鹼的電流效率與實例7-9之組合極為類似。當使用較低酸濃度時,酸電流效率增加約10%。此膜組合之平均電流密度比使用ACM膜時略低(相同酸濃度下及在25V恆定堆疊電壓下操作時為約10mA/cm2)。外部AC阻抗量測證實,在Li2SO4溶液中量測時,AAV電阻高於ACM。 The current efficiency of the acid and base of these membranes is very similar to the combination of Examples 7-9. When a lower acid concentration is used, the acid current efficiency is increased by about 10%. The average current density of this film combination was slightly lower than when using an ACM film (about 10 mA/cm 2 at the same acid concentration and when operating at a constant stack voltage of 25V). External AC impedance measurements confirmed that the AAV resistance was higher than ACM when measured in Li 2 SO 4 solution.

欲再循環至製備磷酸鋰鐵之過程中的氫氧化鋰產物之純度極其重要。使用此鹽裂解技術得出LiOH流中之主要雜質為硫酸根離子,其自酸室穿過雙極膜輸送至鹼中。輸送量應與酸濃度直接相關。藉由比較實例9與實例10(見表3),及比較實例11與實例12(見表4)清楚可見。在各種狀況下,當酸濃度自1M降至0.6M時,1.88M LiOH中之硫酸根污染減少約一半。穩態硫酸根濃度分別為430ppm及200 ppm。 The purity of the lithium hydroxide product to be recycled to the process of preparing lithium iron phosphate is extremely important. Using this salt cracking technique, the main impurity in the LiOH stream is the sulfate ion, which is transported from the acid chamber through the bipolar membrane to the base. The amount of transport should be directly related to the acid concentration. It is clearly seen by comparing Example 9 with Example 10 (see Table 3), and Comparative Example 11 and Example 12 (see Table 4). Under various conditions, when the acid concentration was lowered from 1 M to 0.6 M, the sulfate contamination in 1.88 M LiOH was reduced by about half. Steady-state sulfate concentrations of 430ppm and 200, respectively Ppm.

由於硫酸根離子及鋰離子穿過離子交換膜進行輸送,則因離子水合(電滲)及滲透作用,水亦發生轉移。然而,水輸送至中央室外不足以保持濃度恆定。藉由考慮實例8中水的轉移而說明此情況。一個鋰離子穿過陽離子膜發生轉移,則7個水亦發生轉移。類似地,平均有1.8個水與硫酸根離子一起轉移,一個硫酸鋰共有15.8個水。由於進料溶液中硫酸鋰僅為1莫耳,故每個硫酸鋰幾乎含有55莫耳水,使得中央室中硫酸鋰得到連續稀釋。自進料室中移除水可控制此連續稀釋,且可藉由例如進行反向滲透來達成控制。 Since sulfate ions and lithium ions are transported through the ion exchange membrane, water is also transferred due to ion hydration (electroosmosis) and osmosis. However, the delivery of water to the central outdoor is not sufficient to maintain a constant concentration. This is illustrated by considering the transfer of water in Example 8. When a lithium ion is transferred through the cation membrane, 7 water is also transferred. Similarly, an average of 1.8 waters are transferred together with sulfate ions, and a single lithium sulfate has a total of 15.8 waters. Since the lithium sulfate in the feed solution is only 1 mole, each lithium sulfate contains almost 55 moles of water, so that the lithium sulfate in the central chamber is continuously diluted. This continuous dilution can be controlled by removing water from the feed chamber and can be controlled by, for example, reverse osmosis.

本文引用之所有參考文獻皆出於所有目的以全文引用的方式併入。 All references cited herein are hereby incorporated by reference in their entirety for all purposes.

溫度35℃,恆定電壓=25,進料pH值控制在3.5。 The temperature was 35 ° C, constant voltage = 25, and the feed pH was controlled at 3.5.

溫度35℃,恆定電壓=25,進料pH值控制在3.5/2.0。 The temperature was 35 ° C, the constant voltage was 25, and the feed pH was controlled at 3.5/2.0.

溫度35℃,恆定電壓=25,進料pH值控制在3.5/2.0。 The temperature was 35 ° C, the constant voltage was 25, and the feed pH was controlled at 3.5/2.0.

圖1:用於自含硫酸鋰之液流中以氫氧化鋰形式回收鋰之雙極電滲析池的示意圖。 Figure 1 : Schematic diagram of a bipolar electrodialysis cell for recovering lithium in the form of lithium hydroxide from a liquid stream containing lithium sulfate.

圖2用於將氫氧化鋰與硫酸鋰再循環至製造磷酸鋰鐵之過程中的簡化硫酸鋰雙極電滲析再循環過程之方塊圖。 Figure 2: Lithium hydroxide and lithium sulfate is recycled to the process for producing lithium iron phosphate of a simplified lithium sulfate bipolar electrodialysis recycle process block of FIG.

圖3:用於將氫氧化鋰與硫酸再循環至製造磷酸鋰鐵之過程中的硫酸鋰雙極電滲析再循環過程之方塊圖。 Figure 3 : Block diagram of a lithium sulfate bipolar electrodialysis recycle process for recycling lithium hydroxide and sulfuric acid to the manufacture of lithium iron phosphate.

圖4:使用再循環之氫氧化鋰、硫酸及由另一鋰源產生之氫氧化鋰製造磷酸鋰鐵的硫酸鋰雙極電滲析再循環過程之方塊圖。 Figure 4 : A block diagram of a lithium sulfate bipolar electrodialysis recycle process using recycled lithium hydroxide, sulfuric acid, and lithium hydroxide produced from another lithium source to produce lithium iron phosphate.

圖5:在將預處理至pH 10之進料溶液通入帶有Astom膜之電滲析池的過程中,電流密度隨時間變化之曲線圖。 Figure 5 : A graph of current density as a function of time during the passage of a feed solution pretreated to pH 10 into an electrodialysis cell with an Astom membrane.

圖6:在將預處理至pH 11之進料溶液通入電滲析池的過程中,電流密度以及酸與鹼產物之濃度隨時間變化之曲線圖。 Figure 6 : A plot of current density and concentration of acid and base product over time during the passage of a feed solution pretreated to pH 11 into an electrodialysis cell.

圖7:在將進料溶液通入恆定電壓下操作之Eurodia EUR-2c電滲析池的過程中,電流密度隨時間變化之曲線圖。 Figure 7 : Graph of current density as a function of time during the operation of the Eurodia EUR-2c electrodialysis cell operated with a feed solution at a constant voltage.

Claims (35)

一種以氫氧化鋰形式回收鋰之方法,其包含將含硫酸鋰之水溶液流饋入雙極電滲析池中,其中該池形成氫氧化鋰溶液。 A method of recovering lithium in the form of lithium hydroxide comprising feeding an aqueous solution containing lithium sulfate into a bipolar electrodialysis cell, wherein the cell forms a lithium hydroxide solution. 如請求項1之方法,其包括以下步驟:(a)將含硫酸鋰液流饋入含有雙極電滲析池之裝置中;(b)對該含硫酸鋰溶液進行電滲析以分離帶正電之鋰離子及帶負電之離子;(c)回收自該電滲析分離步驟得到的呈氫氧化鋰溶液形式之鋰。 The method of claim 1, comprising the steps of: (a) feeding a lithium sulfate-containing liquid stream into the apparatus containing the bipolar electrodialysis cell; (b) electrodialyzing the lithium sulfate-containing solution to separate the positively charged one. Lithium ions and negatively charged ions; (c) lithium recovered in the form of a lithium hydroxide solution obtained from the electrodialysis separation step. 如請求項1之方法,其中將該氫氧化鋰饋入需要該氫氧化鋰之過程液流中。 The method of claim 1 wherein the lithium hydroxide is fed to a process stream in which the lithium hydroxide is required. 如請求項1之方法,其中將該氫氧化鋰饋入需要該氫氧化鋰之需氫氧化鋰過程中,使得該需氫氧化鋰過程係連續進行。 The method of claim 1, wherein the lithium hydroxide is fed into a lithium hydroxide-requiring process in which the lithium hydroxide is required, so that the lithium hydroxide-requiring process is continuously performed. 如請求項1之方法,其中該進料流係用於製備磷酸鋰鐵。 The method of claim 1, wherein the feed stream is used to prepare lithium iron phosphate. 如請求項1之方法,其中該液流包含來自鋰源之鋰離子,該鋰源係選自由碳酸鋰、單水合氫氧化鋰及硝酸鋰組成之群。 The method of claim 1, wherein the liquid stream comprises lithium ions from a lithium source selected from the group consisting of lithium carbonate, lithium hydroxide monohydrate, and lithium nitrate. 如請求項1之方法,其中該液流係藉由自含鋰礦石或基於含鋰礦石之材料中提取鋰而得到。 The method of claim 1, wherein the liquid stream is obtained by extracting lithium from a lithium-containing ore or a material based on a lithium-containing ore. 如請求項2之方法,其進一步包含將自電滲析分離所回收之氫氧化鋰再循環至需要該氫氧化鋰之過程中所用之 進料流中。 The method of claim 2, further comprising recycling the lithium hydroxide recovered from the electrodialysis separation to the process required for the lithium hydroxide In the feed stream. 如請求項2之方法,其進一步包含在雙極電滲析之前減少或移除進料流中之磷酸根離子。 The method of claim 2, further comprising reducing or removing phosphate ions in the feed stream prior to bipolar electrodialysis. 一種藉由使用雙極電滲析池來分離含硫酸鋰液流中之離子物質的雙極電滲析裝置,其中該雙極電滲析池包含:(a)陰離子可滲透膜,其允許帶負電之離子通過,但阻止帶正電之鋰離子通過;(b)陽離子可滲透膜,其允許帶正電之鋰離子通過,但阻止帶負電之離子通過;(c)位於陰離子可滲透膜與陽離子可滲透膜之間的雙極膜,其分別與該陰離子可滲透膜及該陽離子可滲透膜形成獨立腔室;(d)陽極與陰極,其中該陰離子可滲透膜、該陽離子可滲透膜及該雙極膜係位於該陽極與該陰極之間;及(e)施加於該等電極兩端的直流電。 A bipolar electrodialysis unit for separating ionic species in a lithium sulfate-containing liquid stream by using a bipolar electrodialysis cell, wherein the bipolar electrodialysis cell comprises: (a) an anion permeable membrane that allows negatively charged ions Pass, but prevent positively charged lithium ions from passing through; (b) a cation permeable membrane that allows positively charged lithium ions to pass, but prevents negatively charged ions from passing through; (c) is located in an anion permeable membrane and cation permeable a bipolar membrane between the membranes forming a separate chamber with the anion permeable membrane and the cationic permeable membrane, respectively; (d) an anode and a cathode, wherein the anion permeable membrane, the cationic permeable membrane, and the bipolar a membrane is located between the anode and the cathode; and (e) a direct current applied across the electrodes. 如請求項10之雙極膜,其中該雙極膜係由陰離子交換層及陽離子交換層形成,且該等層係結合在一起。 The bipolar membrane of claim 10, wherein the bipolar membrane is formed from an anion exchange layer and a cation exchange layer, and the layers are bonded together. 如請求項11之雙極膜,其進一步包含水擴散層或界面,以允許來自外部水性鹽溶液之水擴散。 The bipolar membrane of claim 11 further comprising a water diffusion layer or interface to allow diffusion of water from the external aqueous salt solution. 如請求項10之膜,其係來自市售來源。 The film of claim 10 is from a commercially available source. 如請求項13之膜,其係來自選自由Astom之ACM、CMB、AAV、BP或FumaTech FKB組成之群的市售來源。 The membrane of claim 13 is from a commercially available source selected from the group consisting of ACM, CMB, AAV, BP or FumaTech FKB of Astom. 如請求項10之膜,其係以其對無用離子回遷之抗性、低 電阻率及對所得酸與鹼溶液之潛在腐蝕性質的抗性組合使用。 The membrane of claim 10 is resistant to unwanted ion migration, low The resistivity and the resistance to the potential corrosion properties of the resulting acid to the base solution are used in combination. 如請求項1之方法,其中該進料流含有呈硫酸鋰形式之鋰離子,該方法包含以下步驟:(a)將硫酸鋰液流饋入含有雙極電滲析池之裝置中;(b)對該硫酸鋰液流進行電滲析,以分離帶正電之鋰離子及帶負電之硫酸根離子;(c)在陽極側產生氫氧化鋰溶液且在陰極側產生硫酸溶液;及(d)回收自該雙極電滲析得到的呈氫氧化鋰溶液形式之鋰。 The method of claim 1, wherein the feed stream contains lithium ions in the form of lithium sulfate, the method comprising the steps of: (a) feeding a lithium sulfate stream into a device containing a bipolar electrodialysis cell; (b) The lithium sulfate liquid stream is subjected to electrodialysis to separate positively charged lithium ions and negatively charged sulfate ions; (c) generating a lithium hydroxide solution on the anode side and generating a sulfuric acid solution on the cathode side; and (d) recovering from The bipolar electrodialysis gives lithium in the form of a lithium hydroxide solution. 如請求項16之方法,其中該含硫酸鋰之液流為來自鋰電池組分生產中之進料流。 The method of claim 16, wherein the lithium sulfate-containing liquid stream is a feed stream from the production of lithium battery components. 如請求項16之方法,其進一步包含以下步驟:(a)藉由添加鹼金屬氫氧化物將該硫酸鋰液流之pH值調整至10至11以移除雜質;(b)使雜質自該硫酸鋰液流中沈澱出;(c)自該硫酸鋰液流中過濾雜質;及(d)將所得液流之pH值調整至pH 1至4,隨後將該液流饋入該雙極電滲析裝置中。 The method of claim 16, further comprising the steps of: (a) adjusting the pH of the lithium sulfate stream to 10 to 11 by adding an alkali metal hydroxide to remove impurities; and (b) removing impurities therefrom. Precipitating in the lithium sulfate stream; (c) filtering impurities from the lithium sulfate stream; and (d) adjusting the pH of the resulting stream to pH 1 to 4, and then feeding the stream to the bipolar In the dialysis unit. 如請求項18之方法,其中該鹼金屬氫氧化物係選自由氫氧化鋰、氫氧化鈉及氫氧化鉀組成之群。 The method of claim 18, wherein the alkali metal hydroxide is selected from the group consisting of lithium hydroxide, sodium hydroxide, and potassium hydroxide. 如請求項18之方法,其中該雜質為磷酸鹽。 The method of claim 18, wherein the impurity is a phosphate. 如請求項18之方法,其中步驟(d)之該硫酸鋰液流之pH值 係經調整至2至3.5。 The method of claim 18, wherein the pH of the lithium sulfate stream in step (d) is It is adjusted to 2 to 3.5. 如請求項18之方法,其中步驟(d)之該硫酸鋰液流之pH值係經調整至2至3。 The method of claim 18, wherein the pH of the lithium sulfate stream of step (d) is adjusted to 2 to 3. 如請求項16之方法,其進一步包含藉由使用離子交換膜自該硫酸鋰液流中移除磷酸鹽,隨後將該液流饋入該雙極電滲析裝置中。 The method of claim 16, further comprising removing phosphate from the lithium sulfate stream by using an ion exchange membrane, and subsequently feeding the stream into the bipolar electrodialysis unit. 如請求項16之方法,其中將該氫氧化鋰溶液引入製備LiFePO4或其他含鋰鹽或產物之過程中。 The method of claim 16, wherein the lithium hydroxide solution is introduced into the process of preparing LiFePO 4 or other lithium-containing salt or product. 如請求項16之方法,其中該所回收之氫氧化鋰係用作化學反應中之鹼。 The method of claim 16, wherein the recovered lithium hydroxide is used as a base in a chemical reaction. 如請求項16之方法,其中該氫氧化鋰溶液係用於調整含硫酸鋰之進料流的pH值。 The method of claim 16, wherein the lithium hydroxide solution is used to adjust the pH of the lithium sulfate-containing feed stream. 如請求項16之方法,其進一步包含濃縮該氫氧化鋰溶液。 The method of claim 16, further comprising concentrating the lithium hydroxide solution. 如請求項16之方法,其進一步包含純化該氫氧化鋰溶液。 The method of claim 16, which further comprises purifying the lithium hydroxide solution. 如請求項16之方法,其進一步包含以下步驟:(a)回收自該雙極電滲析產生的該硫酸溶液;(b)向該所回收之硫酸溶液中添加鐵源;(c)使該硫酸溶液轉化成硫酸鐵;(d)混合該硫酸根離子、該所回收之氫氧化鋰溶液及磷酸鹽原料以製備磷酸鋰鐵,其中該磷酸鋰係於連續過程中產生。 The method of claim 16, further comprising the steps of: (a) recovering the sulfuric acid solution produced by the bipolar electrodialysis; (b) adding an iron source to the recovered sulfuric acid solution; (c) causing the sulfuric acid The solution is converted into iron sulfate; (d) the sulfate ion, the recovered lithium hydroxide solution and the phosphate raw material are mixed to prepare lithium iron phosphate, wherein the lithium phosphate is produced in a continuous process. 如請求項29之方法,其中該鐵源為天然存在之鐵礦石中 所見之金屬鐵。 The method of claim 29, wherein the source of iron is naturally occurring iron ore Metal iron seen. 如請求項29之方法,其中藉由自另一來源引入氫氧化鋰將該所回收之氫氧化鋰溶液調整至所需氫氧化鋰濃度。 The method of claim 29, wherein the recovered lithium hydroxide solution is adjusted to a desired lithium hydroxide concentration by introducing lithium hydroxide from another source. 如請求項29之方法,其中藉由濃縮所回收之氫氧化鋰溶液將該所回收之氫氧化鋰溶液調整至所需氫氧化鋰濃度。 The method of claim 29, wherein the recovered lithium hydroxide solution is adjusted to a desired lithium hydroxide concentration by concentrating the recovered lithium hydroxide solution. 如請求項29之方法,其進一步包含以下步驟:(a)藉由添加鹼金屬氫氧化物將該硫酸鋰液流之pH值調整至10至11以移除雜質;(b)使雜質自該硫酸鋰液流中沈澱出;(c)自該硫酸鋰液流中過濾雜質;及(d)將所得液流之pH值調整至pH 2至3.5,隨後將該液流饋入該雙極電滲析裝置中。 The method of claim 29, further comprising the steps of: (a) adjusting the pH of the lithium sulfate stream to 10 to 11 by adding an alkali metal hydroxide to remove impurities; and (b) removing impurities therefrom. Precipitating in the lithium sulfate stream; (c) filtering impurities from the lithium sulfate stream; and (d) adjusting the pH of the resulting stream to pH 2 to 3.5, and then feeding the stream to the bipolar In the dialysis unit. 如請求項16之方法,其進一步包含:(a)回收該雙極電滲析所得之該氫氧化鋰液流與該硫酸液流;(b)使該硫酸液流與碳酸鋰反應以產生額外的硫酸鋰溶液;(c)向含硫酸鋰之原始進料流中添加該額外硫酸鋰溶液;及(d)向該雙極電滲析裝置中連續饋入該硫酸鋰液流。 The method of claim 16, further comprising: (a) recovering the lithium hydroxide liquid stream obtained by the bipolar electrodialysis and the sulfuric acid liquid stream; (b) reacting the sulfuric acid liquid stream with lithium carbonate to produce additional a lithium sulfate solution; (c) adding the additional lithium sulfate solution to the original feed stream containing lithium sulfate; and (d) continuously feeding the lithium sulfate liquid stream to the bipolar electrodialysis unit. 如請求項34之方法,其進一步包含以下步驟:(a)藉由添加鹼金屬氫氧化物將該硫酸鋰液流之pH值調整至10至11以移除雜質; (b)使雜質自該硫酸鋰液流中沈澱出;(c)自該硫酸鋰液流中過濾雜質;及(d)將所得液流之pH值調整至pH 2至3.5,隨後將該液流饋入該雙極電滲析裝置中。 The method of claim 34, further comprising the steps of: (a) adjusting the pH of the lithium sulfate stream to 10 to 11 by adding an alkali metal hydroxide to remove impurities; (b) precipitating impurities from the lithium sulfate stream; (c) filtering impurities from the lithium sulfate stream; and (d) adjusting the pH of the resulting stream to pH 2 to 3.5, followed by the liquid The flow is fed into the bipolar electrodialysis unit.
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