WO2020185645A1 - Method for concentrating and purifying eluate brine for the production of a purified lithium compound - Google Patents
Method for concentrating and purifying eluate brine for the production of a purified lithium compound Download PDFInfo
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- WO2020185645A1 WO2020185645A1 PCT/US2020/021640 US2020021640W WO2020185645A1 WO 2020185645 A1 WO2020185645 A1 WO 2020185645A1 US 2020021640 W US2020021640 W US 2020021640W WO 2020185645 A1 WO2020185645 A1 WO 2020185645A1
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D15/00—Lithium compounds
- C01D15/08—Carbonates; Bicarbonates
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction, e.g. ion-exchange, ion-pair, ion-suppression or ion-exclusion
- B01D15/361—Ion-exchange
- B01D15/362—Cation-exchange
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/025—Reverse osmosis; Hyperfiltration
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/027—Nanofiltration
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/029—Multistep processes comprising different kinds of membrane processes selected from reverse osmosis, hyperfiltration or nanofiltration
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01D61/42—Electrodialysis; Electro-osmosis ; Electro-ultrafiltration; Membrane capacitive deionization
- B01D61/422—Electrodialysis
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D61/42—Electrodialysis; Electro-osmosis ; Electro-ultrafiltration; Membrane capacitive deionization
- B01D61/44—Ion-selective electrodialysis
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01D61/42—Electrodialysis; Electro-osmosis ; Electro-ultrafiltration; Membrane capacitive deionization
- B01D61/44—Ion-selective electrodialysis
- B01D61/46—Apparatus therefor
- B01D61/463—Apparatus therefor comprising the membrane sequence AC or CA, where C is a cation exchange membrane
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/58—Multistep processes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D9/00—Crystallisation
- B01D9/0018—Evaporation of components of the mixture to be separated
- B01D9/0031—Evaporation of components of the mixture to be separated by heating
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- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J47/00—Ion-exchange processes in general; Apparatus therefor
- B01J47/12—Ion-exchange processes in general; Apparatus therefor characterised by the use of ion-exchange material in the form of ribbons, filaments, fibres or sheets, e.g. membranes
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction, e.g. ion-exchange, ion-pair, ion-suppression or ion-exclusion
- B01D15/361—Ion-exchange
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D9/00—Crystallisation
- B01D2009/0086—Processes or apparatus therefor
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2311/00—Details relating to membrane separation process operations and control
- B01D2311/06—Specific process operations in the permeate stream
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- B01D2311/25—Recirculation, recycling or bypass, e.g. recirculation of concentrate into the feed
- B01D2311/251—Recirculation of permeate
- B01D2311/2512—Recirculation of permeate to feed side
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D2311/25—Recirculation, recycling or bypass, e.g. recirculation of concentrate into the feed
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- B01D2311/2523—Recirculation of concentrate to feed side
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01D2311/00—Details relating to membrane separation process operations and control
- B01D2311/26—Further operations combined with membrane separation processes
- B01D2311/2623—Ion-Exchange
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01D2311/00—Details relating to membrane separation process operations and control
- B01D2311/26—Further operations combined with membrane separation processes
- B01D2311/2642—Aggregation, sedimentation, flocculation, precipitation or coagulation
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D2311/00—Details relating to membrane separation process operations and control
- B01D2311/26—Further operations combined with membrane separation processes
- B01D2311/2643—Crystallisation
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2311/00—Details relating to membrane separation process operations and control
- B01D2311/26—Further operations combined with membrane separation processes
- B01D2311/2673—Evaporation
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- C—CHEMISTRY; METALLURGY
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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- C—CHEMISTRY; METALLURGY
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- C02F1/00—Treatment of water, waste water, or sewage
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- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
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- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
- C02F1/4693—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrodialysis
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- C—CHEMISTRY; METALLURGY
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- C—CHEMISTRY; METALLURGY
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F2001/5218—Crystallization
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
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- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Definitions
- the present invention relates to the recovery and purification of lithium and to a process that employs electrodialysis to separate lithium ions from a feed solution containing lithium and various impurities.
- lithium is an abundant element. There are, however, few commercial resources where lithium is found in
- lithium concentrations sufficient for producing useful lithium compounds.
- the primary sources of lithium are in brines from salars and salt lakes and ores.
- Geothermal brines are another source for lithium.
- a large percentage of lithium chloride and lithium carbonate and their derivatives are commercially produced from the recovery of lithium from brines, typically via natural evaporative processes.
- lithium is extracted from a brine drawn from a solar pond by an elution process that produces a solution rich in lithium, sodium chloride and various impurities.
- Typical impurities include calcium, magnesium, sulfate, along with silica and boron, such as silica, magnesium and calcium.
- One current approach to purifying brines rich in lithium is through reverse osmosis and evaporation. This approach typically results in the production of a concentrate containing large amounts of scaling species, such as silica. The presence of such large amounts of silica tends to scale the concentrating system. In order to overcome this scaling, additional pre-treatment steps are required to remove scaling compounds prior to final concentration in an evaporator or crystallizer system.
- the present invention in one embodiment, relates to a method of purifying an extraction eluate rich in lithium, sodium chloride, but containing impurities, such as calcium, magnesium, sulfate and silica.
- the extraction eluate is directed to a nanofiltration unit or a softening process that removes sulfate and associated calcium and magnesium.
- Permeate from the nanofiltration unit or the effluent from the softening process is directed to and through an electrodialysis unit. Prior to reaching the electrodialysis unit, steps are taken, if required, to maintain a substantial portion of the silica or another impurity as non-ionized.
- the lithium, sodium and chloride ions pass from the solution through a cation-transfer membrane and an anion-transfer membrane to concentrate compartments in the electrodialysis unit.
- An aqueous solution is circulated through the concentrate compartments and collects the lithium, sodium and chloride ions to produce a brine rich in lithium, sodium and chloride ions.
- the electrodialysis unit also produces a product stream which is deficient in lithium, sodium and chloride but which contains the non-ionized impurities, such as silica. Concentrate from the electrodialysis unit is subjected to a precipitation process that produces lithium carbonate that is subsequently subjected to a purification process.
- a lithium carbonate purification process is carried out without nanofiltration or softening.
- the extraction eluate is directed into an electrodialysis unit comprising monovalent selective cation and anion exchange membranes.
- the monovalent cation and anion membranes preferentially transfer monovalent cations and anions (in this embodiment lithium, sodium and chloride ions) to concentrate compartments where they are collected by an aqueous solution or demineralized water to form a concentrate rich in lithium, sodium and chloride but which may contain some hardness in the form of calcium and magnesium, for example.
- the concentrate is then directed to an ion exchange unit, such as a chelating ion exchange unit, to remove hardness. Thereafter, lithium (in the form of either carbonate, for example) can be removed from the concentrate.
- Figure 1 is a schematic illustration of a lithium recovery process.
- Figure 2 is a schematic illustration of an electrodialysis unit and illustrates the separation of lithium, sodium and chloride ions from a feed.
- FIG. 3 is a schematic illustration of the lithium recovery process showing how an electrodialysis process is integrated into other steps of the lithium recovery process.
- the present invention relates to a process for recovering lithium.
- Lithium is a highly reactive alkali metal that offers excellent heat and electrical conductivity. These properties make lithium particularly useful for lithium ion batteries for electric cars and consumer electronics, as well as useful for pharmaceutical and chemical applications. Because of its high reactivity, pure elemental lithium is not found in nature but is instead present as a constituent of salts and other compounds. Most commercial lithium is available in the form of lithium carbonate which is a relatively stable compound that can easily be converted to other salts or chemicals.
- Lithium salts are found in underground deposits of brine, mineral ore as well as sea water and geothermal brines. While lithium is fairly abundant, not all lithium sources are deemed economically viable at this time. Generally speaking, however, commercial lithium arises from two main sources: underground brine and mineral ore deposits. A large amount of today's lithium is recovered from liquid brine reservoirs located beneath salt flats, known as salars. Other lithium-rich brine resources include geothermal and oil field brines.
- Lithium recovery in general is a relatively long process.
- drilling is generally required to access the brine deposits.
- the brine containing lithium is pumped to the surface and placed in solar ponds where an evaporation process takes place. Brine remains in the solar ponds until most of the water content has been removed through solar evaporation.
- Salar brines for example, are concentrated and in addition to lithium, typically contain sodium, chloride, as well as any number of impurities such as sulfate, silica and/or boron.
- FIG 1 is a diagrammatic view showing one embodiment of a lithium recovery process.
- the process is referred to generally by the numeral 10.
- the brine is pumped from the solar pond and subjected to a process that is referred to in Figure 1 as natural brine preparation and filtration 12.
- This process can vary depending on the makeup of the brine and the particular processes that follow. In many cases, some type of filtration is employed to remove suspended solids from the brine. In addition, this process may employ other means to precipitate or otherwise remove certain impurities from the brine at this stage.
- the brine is rich in lithium and, in the present example, includes sodium chloride and other impurities.
- the impurities in the brine can vary based on the source of the brine.
- the impurities include sulfate, silica and/or boron, along with hardness in the form of calcium and magnesium. There may also be small trace amounts of transitional metals.
- the brine is subjected to a lithium extraction process 14.
- lithium is extracted from the effluent from the natural brine preparation and filtration stage discussed above.
- Various lithium extraction processes can be employed and people skilled in the art appreciate various lithium extraction processes.
- an adsorption process can be employed for extracting lithium from the brine.
- Various adsorbents or resins can be used.
- lithium selective ion exchange adsorbents can be used for extracting lithium from brines.
- Inorganic ion exchange adsorbents such as lithium manganese dioxide, spinel lithium titanium oxides and lithium aluminum layered double hydroxide chloride are known to have high lithium selective uptake capacity.
- the lithium extraction process 14 produces a brine rich in lithium and sodium chloride and having a range of impurities, such as silica, sulfate, boron, calcium and magnesium.
- the total suspended solids in the brine can be approximately 1 1 ,000 mg/L and contain approximately 20 mg/L of silica, 100 mg/L of boron, 50 mg/L of sulfate and approximately 50 mg/L of calcium, as well as
- the process focuses on removing some impurities from the lithium-rich brine.
- the sulfate, calcium and magnesium is first addressed.
- Various approaches such as nanofiltration, chemical softening or ion exchange softening, can be employed.
- the lithium-rich brine is subjected to a nanofiltration process which produces a reject stream containing sulfate and calcium and magnesium associated with the sulfate. Tests indicate that 95%-99% of the sulfate can typically be removed from the lithium-rich brine.
- the permeate from the nanofiltration process will continue to be a brine rich in lithium and sodium chloride and may include some residual hardness (calcium and magnesium), along with other impurities which, in this example, are principally silica and boron. It is contemplated that, in some cases, the permeate from the nanofiltration process will contain 90% wt. of lithium and sodium chloride.
- Electrodialysis unit 16 includes a cathode 16A and an anode 16B. Between the cathode 16A and the anode 16B is a cation transfer membrane 16C and an anion-transfer membrane 16D. This forms two concentrate compartments 16E and 16F and a center product compartment 16G.
- the feed to the electrodialysis unit 16 is rich in lithium, sodium and chloride ions, but there are still impurities in the feed.
- the process takes steps to maintain these impurities in a non-ionized state. If the impurity is non-ionized, it will not pass through the cation-transfer membrane 16A or the anion-transfer membrane 16D but will remain in the product compartment 16G and ultimately will be a constituent of the demineralized product that leaves the product compartment. See Figure 2.
- the impurities include silica and/or boron.
- the process aims to maintain the silica and/or boron in the feed non-ionized.
- Silicon (Si) is primarily present as Si0 2 in water at an acid or neutral pH.
- the silica becomes ionized by the formation of HSi03 which is how the silica solubility and rejection is increased in high pH reverse osmosis processes.
- HSi03 is how the silica solubility and rejection is increased in high pH reverse osmosis processes.
- substantially all of the silica in the feed is non-ionized and passes through the electrodialysis unit 16 and form a part of the demineralized product.
- the pH of the feed to the electrodialysis unit 16 is monitored and maintained at or below 7.
- the lithium and sodium ions having a positive charge pass through the cation-transfer membrane 16C into compartment 16E.
- Chloride being a negative ion, passes through the anion-transfer membrane 16D to compartment 16F.
- a selected medium sometimes referred to as a dilute stream, such as demineralized water, is circulated through the concentrate compartments 16E and 16F to collect the lithium, sodium and chloride ions.
- the dilute stream with the collected lithium, sodium and chloride ions are merged and thereafter split and recycled through the concentrate compartments 16E and 16F, all the while continuing to collect lithium, sodium and chloride ions.
- the product stream from the electrodialysis unit 16 is directed to an RO system that concentrates the product stream. That is, the RO system concentrates the impurities in the product stream, which in this example are silica and/or boron.
- the RO system produces permeate that is directed to the lithium extraction unit 14.
- Concentrate from the RO system is referred to as a waste brine and is directed to a waste brine silica/boron management unit. See Figure 1.
- the concentrate from the RO system, including the impurities that were present in the product stream, can be further treated.
- the impurities in the concentrate produced by the electrodialysis unit 16 require removal through thermal evaporation or crystallization. This is, however, optional in many cases. Even if required, the amount of impurities in the concentrate may still be sufficiently low that only a relatively small thermal evaporation and crystallization is required.
- the electrodialysis concentrate might still contain residual hardness above a trace amount, as well as transition metals. Residual hardness can be removed by ion exchange softening.
- Figure 1 refers to this as brine polishing IX.
- Various ion exchange types can be employed. For example, chelating ion exchange resin can be employed to remove residual hardness, as well as transition metals not removed by the nanofiltration process.
- the effluent is subjected to a precipitation process that precipitates lithium carbonate.
- a precipitation process that precipitates lithium carbonate.
- reagents can be employed at this stage to precipitate substantially pure lithium compounds.
- sodium carbonate is mixed with the lithium, sodium and chloride-rich stream to cause the precipitation of lithium carbonate.
- various processes can be employed for the purification of lithium carbonate. See Figure 1.
- FIG. 3 is a schematic illustration that depicts how the electrodialysis unit 16 is integrated into the overall lithium recovery process.
- the source of the lithium-containing brine, the lithium extraction process, and the nanofiltration process has been described above.
- the permeate from the nanofiltration unit is rich in lithium, sodium and chloride ions.
- the permeate is directed into the center compartment 16G of the electrodialysis unit 16.
- the lithium and sodium ions pass to the concentrate compartment 16E while the chloride ions pass to the concentrate compartment 16F.
- the concentrates produced by the electrodialysis unit 16 is recycled through the electrodialysis unit and in the process continues to collect lithium, sodium and chloride ions.
- a portion of the concentrate being recycled through the electrodialysis unit 16 is separated and directed through a number of processes discussed above. These include the optional thermal evaporation/crystallization process, brine polishing ion exchange treatment, lithium carbonate precipitation and lithium carbonate purification.
- the product stream containing the impurities is directed to a reverse osmosis system where the impurities are concentrated into an RO concentrate and then directed to a waste management unit. See Figure 3.
- the permeate from the reverse osmosis system is recycled back to the lithium extraction process.
- an alternative process might include an electrodialysis unit which employs monovalent selective cation and anion exchange membranes followed by chelating ion exchange.
- Electrodialysis using monovalent selective membranes utilizes membranes that preferentially transport monovalent anions or monovalent cations.
- Using a monovalent selective electrodialysis process would enable eliminating the nanofiltration process discussed above while also separating silica and/or boron scaling components from the concentrate solution.
- Concentrate from the electrodialysis process may further include treatment through a chelating ion exchange process in order to remove hardness ions since the monovalent selective membranes do not have a 100% rejection rate for divalent ions.
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- Materials Engineering (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
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Abstract
Description
Claims
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CA3132970A CA3132970C (en) | 2019-03-13 | 2020-03-09 | Method for concentrating and purifying eluate brine for the production of a purified lithium compound |
| US17/438,495 US12258280B2 (en) | 2019-03-13 | 2020-03-09 | Method for concentrating and purifying eluate brine for the production of a purified lithium compound |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US201962817624P | 2019-03-13 | 2019-03-13 | |
| US62/817,624 | 2019-03-13 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2020185645A1 true WO2020185645A1 (en) | 2020-09-17 |
Family
ID=70110383
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/US2020/021640 Ceased WO2020185645A1 (en) | 2019-03-13 | 2020-03-09 | Method for concentrating and purifying eluate brine for the production of a purified lithium compound |
Country Status (5)
| Country | Link |
|---|---|
| US (1) | US12258280B2 (en) |
| AR (1) | AR115297A1 (en) |
| CA (1) | CA3132970C (en) |
| CL (1) | CL2021002371A1 (en) |
| WO (1) | WO2020185645A1 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114634169A (en) * | 2022-03-14 | 2022-06-17 | 浙江志澄环境资源科技有限公司 | Coupling lithium extraction method of chemical precipitation and replacement electrodialysis |
| CN114671554A (en) * | 2020-12-24 | 2022-06-28 | 大连波美科技有限公司 | Zero-discharge sewage system containing guanidine salt and application method |
| WO2023091981A1 (en) * | 2021-11-18 | 2023-05-25 | Energy Exploration Technologies, Inc. | Systems and methods for direct lithium extraction |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114620750B (en) * | 2020-12-14 | 2023-10-27 | 中蓝长化工程科技有限公司 | A process for extracting lithium from sodium sulfate subtype salt lake brine |
| CN114870633B (en) * | 2022-05-18 | 2023-04-14 | 北京万邦达环保技术股份有限公司 | Process for enriching lithium in salt lake brine |
| CN114789000B (en) * | 2022-05-25 | 2024-01-30 | 南开大学 | Modified cation exchange membrane for electrodialysis desalination of high-salt ethylene glycol solution, modification method, electrodialysis device and desalination method |
| CN116199385B (en) * | 2023-03-03 | 2025-11-25 | 北京华特源科技有限公司 | A method for separating monovalent and polyvalent ions in water and a method for lithium extraction from salt lakes |
| WO2024259211A2 (en) * | 2023-06-16 | 2024-12-19 | Energy Exploration Technologies, Inc. | Compositions, systems and methods for recovering a metal from an aqueous solution |
Citations (4)
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|---|---|---|---|---|
| WO2011133165A1 (en) * | 2010-04-23 | 2011-10-27 | Simbol Mining Corp. | A process for making lithium carbonate from lithium chloride |
| US8741256B1 (en) * | 2009-04-24 | 2014-06-03 | Simbol Inc. | Preparation of lithium carbonate from lithium chloride containing brines |
| CN107298450A (en) * | 2016-08-31 | 2017-10-27 | 江苏力泰锂能科技有限公司 | The method that lithium hydroxide and lithium carbonate are prepared using soluble lithium salt solution |
| CN107399747A (en) * | 2017-08-17 | 2017-11-28 | 江苏久吾高科技股份有限公司 | A kind of method and device that lithium is carried from salt lake brine with high magnesium-lithium ratio |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| AU2015408086A1 (en) | 2015-08-28 | 2018-03-15 | Albemarle Corporation | Processes for recovering lithium values from lithium-containing brines |
| WO2018208305A1 (en) * | 2017-05-11 | 2018-11-15 | Bl Technologies, Inc. | Method for softening lithium brine using nanofiltration |
-
2019
- 2019-05-28 AR ARP190101445A patent/AR115297A1/en active IP Right Grant
-
2020
- 2020-03-09 CA CA3132970A patent/CA3132970C/en active Active
- 2020-03-09 WO PCT/US2020/021640 patent/WO2020185645A1/en not_active Ceased
- 2020-03-09 US US17/438,495 patent/US12258280B2/en active Active
-
2021
- 2021-09-10 CL CL2021002371A patent/CL2021002371A1/en unknown
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US8741256B1 (en) * | 2009-04-24 | 2014-06-03 | Simbol Inc. | Preparation of lithium carbonate from lithium chloride containing brines |
| WO2011133165A1 (en) * | 2010-04-23 | 2011-10-27 | Simbol Mining Corp. | A process for making lithium carbonate from lithium chloride |
| CN107298450A (en) * | 2016-08-31 | 2017-10-27 | 江苏力泰锂能科技有限公司 | The method that lithium hydroxide and lithium carbonate are prepared using soluble lithium salt solution |
| CN107399747A (en) * | 2017-08-17 | 2017-11-28 | 江苏久吾高科技股份有限公司 | A kind of method and device that lithium is carried from salt lake brine with high magnesium-lithium ratio |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114671554A (en) * | 2020-12-24 | 2022-06-28 | 大连波美科技有限公司 | Zero-discharge sewage system containing guanidine salt and application method |
| WO2023091981A1 (en) * | 2021-11-18 | 2023-05-25 | Energy Exploration Technologies, Inc. | Systems and methods for direct lithium extraction |
| EP4423015A4 (en) * | 2021-11-18 | 2025-12-17 | Energy Exploration Tech Inc | SYSTEMS AND PROCESSES FOR DIRECT LITHIUM EXTRACTION |
| CN114634169A (en) * | 2022-03-14 | 2022-06-17 | 浙江志澄环境资源科技有限公司 | Coupling lithium extraction method of chemical precipitation and replacement electrodialysis |
| CN114634169B (en) * | 2022-03-14 | 2023-03-21 | 浙江志澄环境资源科技有限公司 | Coupling lithium extraction method of chemical precipitation and replacement electrodialysis |
Also Published As
| Publication number | Publication date |
|---|---|
| CA3132970A1 (en) | 2020-09-17 |
| US12258280B2 (en) | 2025-03-25 |
| CL2021002371A1 (en) | 2022-06-03 |
| CA3132970C (en) | 2023-09-26 |
| AR115297A1 (en) | 2020-12-23 |
| US20220144655A1 (en) | 2022-05-12 |
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