AU2009356416B2 - Using the solid waste-quicklime membrane SWQM process for the production of sodium hydroxide - Google Patents
Using the solid waste-quicklime membrane SWQM process for the production of sodium hydroxide Download PDFInfo
- Publication number
- AU2009356416B2 AU2009356416B2 AU2009356416A AU2009356416A AU2009356416B2 AU 2009356416 B2 AU2009356416 B2 AU 2009356416B2 AU 2009356416 A AU2009356416 A AU 2009356416A AU 2009356416 A AU2009356416 A AU 2009356416A AU 2009356416 B2 AU2009356416 B2 AU 2009356416B2
- Authority
- AU
- Australia
- Prior art keywords
- liquor
- naoh
- sodium chloride
- acidic
- exchange resin
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Ceased
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D1/00—Oxides or hydroxides of sodium, potassium or alkali metals in general
- C01D1/04—Hydroxides
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B26/00—Obtaining alkali, alkaline earth metals or magnesium
- C22B26/10—Obtaining alkali metals
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D1/00—Oxides or hydroxides of sodium, potassium or alkali metals in general
- C01D1/04—Hydroxides
- C01D1/20—Preparation by reacting oxides or hydroxides with alkali metal salts
- C01D1/22—Preparation by reacting oxides or hydroxides with alkali metal salts with carbonates or bicarbonates
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D7/00—Carbonates of sodium, potassium or alkali metals in general
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D7/00—Carbonates of sodium, potassium or alkali metals in general
- C01D7/07—Preparation from the hydroxides
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- 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
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
-
- 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
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
Abstract
The proposed invention uses ion exchange technology to produce dilute caustic soda liquor from calcium hydroxide liquor Ca(OH)
Description
WO 2011/070384 PCT/IB2009/007713 1 Technical field and Background information Using heat generated from solid waste incineration (or any available source of waste heat) with brine water, acidic water, and advanced membrane and resin technology in the production of soda ash Na2CO3 and sodium hydroxide NaOH. From a pre-limer calcium hydroxide Ca(OH)2 (500 to 1000 ppm) is processed by a cation exchange system (strong or weak) to produce sodium hydroxide (500 to 1000 ppm) such that: Ca(OH)2 + 2R-Na+ -* 2NaOH + R-Ca++ The present invention uses a classical equation where C02 is reacted with caustic soda NaOH to produce clear solution of sodium carbonate Na2CO3 such that: NaOH + C02 -> Na2CO3 Presence of regenerants such as brine water with a salinity of 6 to 12 %, acidic water with acidity of >8% (e.g. HCI or H2SO4) or a combination of both is crucial because it is used to regenerate the cation exchanger such that: (1) R-Ca++ + 2NaCl -- 2R-Na+ + CaCI2 (2) R-Ca++ + HX -- 2R-H + CaX R-H + NaCl -- R-Na+ + HCl (acidic waste) One aspect of the present patent requires a sparging reactor to bubble acidic flue gas where gases such as HCI and S02 can be captured to produce acidic solutions such that, HCI(g) + H20 -> HCl(aq) used for strong ion exchange regeneration S02(g) + H20 + 0 -> H2SO4(aq) used for strong ion exchange regeneration Acidic waste can be combined with basic waste such as power plant ash to produce neutral output that can be discharged safely to environment. Sodium carbonate liquor produced is of low percentage ie 0.05 to 0.5% and need to be concentrated to ~6%. The concentration process is performed using reverse osmosis system where the Na2CO3 liquor is taken through multiple passes until the final concentrate output is around 6%. Industrially a concentration of 6% is low to extract the solid economically a major setback for membrane technology. The difficulty in going above 6% with existing membrane technology is the high pressure that deteriorates the membrane. Even if recompression evaporation is used around 1MW is required to produce one ton of solid product. In the present invention the most obvious heat source is the heat emitted by solid waste incineration or any other waste heat source.
1000778158 2 Reference to any prior art in the specification is not, and should not be taken as, an acknowledgment, or any form of suggestion, that this prior art forms part of the common general knowledge in Australia or any other jurisdiction or that this prior art could reasonably be expected to be ascertained, understood and regarded as relevant by a person skilled in the art. Summary of Invention In one aspect of the invention there is provided a process for producing a Na 2
CO
3 liquor containing at least 50wt% Na 2
CO
3 , the process including: contacting a solution of calcium hydroxide and sodium chloride with an ion exchange resin to form a caustic soda solution containing sodium chloride; sparging the caustic soda solution containing sodium chloride with carbon dioxide and an acidic gas containing HCl or H 2
SO
4 to form a Na 2
CO
3 solution containing sodium chloride; concentrating the Na 2
CO
3 solution containing sodium chloride through reverse osmosis to form the Na 2
CO
3 liquor containing at least 50up to about 6wt% Na 2
CO
3 ; using waste heat to further concentrate the Na 2
CO
3 liquor to a concentration of at least 50wt%. General description The process by which ion exchange technology to produce dilute caustic soda liquor from calcium hydroxide liquor Ca(OH) 2 followed by the reaction of carbon dioxide CO 2 with caustic soda to produce dilute sodium carbonate solution. Multiple reverse osmosis and acidic CO 2 0 sparging can concentrate the Na 2
CO
3 liquor to 6-7%. The 6-7% liquor is treated with waste heat to produce 50% or solid Na 2
CO
3 . The 6-7% liquor can be treated with Ca(OH) 2 to produce 6-7% NaOH liquor then can be transformed to 50% or solid NaOH. The invention requires three chemicals CO 2 , Ca(OH) 2 , and sodium chloride NaCl to produce NaOH. The output of many industrial processes generates waste heat, brine water, and CO 2 and the present invention 5 combines these components in the production of solid Na 2
CO
3 , NaOH or their high % liquors. Availability of waste heat sources can lead to higher efficiency in Na 2
CO
3 and NaOH production. The process is not electrochemical chloro-alkali technology or Solvay process. There 1000778158 2A are similarities in the hardware in patent # PCT/1B2008/002020 but the present patent differs in the mechanism of operation of the ion exchange reverse osmosis system and includes utilization of acidic flue gas. In one or more embodiments, the present invention uses the SWQM process in patent# PCT/1B2008/002020 to eliminate the need for high consumption of electric power as in chloro alkali technology. The use of brine and acidic water and advanced membrane and resin technology in solid waste processing and the production of soda ash Na 2
CO
3 and caustic soda NaOH. The process by which this invention attempts to bring solid waste, brine water waste, acidic water waste extracted from acidic flue gas, and CO 2 waste problems in one industrial process to bring about a green solution through large elimination of the various wastes stated above while making a financial benefit from selling the soda or caustic soda commodity chemical as byproduct of the combined processes. The process which essentially relies on advanced membrane technology systems to produce soda ash Na 2
CO
3 and caustic soda NaOH in certain embodiments includes the following combined stages (i) to (iv): (i) - Sparger design: Acidic flue gas can be sparged under pressure to dissolve the acidic gas in sea water or river water to form acidic liquor that can be used in strong or weak ion exchange regeneration. (ii) -Ion exchange system: Would receive the calcium hydroxide liquor Ca(OH) 2 (e.g. -0.5 g/L) to produce a dilute caustic soda liquor at 1000 ppm concentration or higher depending on the type of ion-exchanger used. (iii) -Reactors design: Carbon dioxide gas is sparged through caustic soda NaOH in a reactor to form a dilute sodium carbonate liquor Na 2
CO
3 (e.g. 700 ppm Na 2
CO
3 to 300 ppm NaOH). The latter is then subjected to further filtration to remove impurity particulates then passed to reverse osmosis system. The low % liquor needs to be converted and concentrated to higher % sodium carbonate Na 2
CO
3 liquor (e.g. 2400 ppm Na 2
CO
3 to 1000 ppm NaOH) by passing it to a reverse osmosis system under controlled pH conditions.
1000778158 2B (iv)-Reverse osmosis (RO) unit contains RO cartridges cascaded with the C0 2 -NaOH reactors in between. The objective is to keep the NaOH concentration below 300 ppm as the concentration of Na 2
CO
3 is increased. Description of how the invention addresses a technical problem Solid waste, brine water waste, and CO 2 waste are major problems faced by human communities worldwide. The proposed invention attempts to bring these three waste problems in one industrial process to bring about a green solution while making a financial benefit. The green solution is fulfilled by large elimination of the various wastes stated above. The financial benefit comes from selling the soda commodity chemicals as byproduct of the combined processes. In a sense the production of NaOH by the WHQM process is an alternative to the chloro-alkali cell process that is used worldwide to produce caustic soda NaOH. Major problem in the chloro alkali cell process it is tied up to chlorine production and chlorine is a poisonous gas that must find a safe storage. Production of caustic soda using WHQM process is chlorine independent. The process essentially relies on advanced membrane technology systems to produce sodium hydroxide NaOH. Therefore, it is very different from chloro-alkali process that works on high consumption of electrical power (i.e. 3000 KWH per ton of NaOH) to convert NaCl to NaOH. In the present invention the only byproduct is CaCO 3 while in chloro-alkali technology dangerous gases such as chlorine and hydrogen have to be handled safely.
WO 2011/070384 PCT/IB2009/007713 3 Detailed description of the invention and description of drawings Heat from solid waste incinerators (or any other waste heat source) can be utilized as discussed in patent # PCT/1B2008/002020. The mechanism of NaOH production follows a similar scheme as the NaHCO3 production as shown in Figure-Ion page 9: Sparger design: Acidic flue gas can be sparged under pressure to dissolve the acidic gas in sea water or river water to form acidic liquor that can be used in strong or weak ion exchange regeneration. Ion exchange system: Would receive the calcium hydroxide liquor Ca(OH)2 (e.g. -0.5-1 g/L) to produce a dilute caustic soda liquor at 1000 ppm concentration. Reactors design: Carbon dioxide gas is sparged through caustic soda NaOH in a reactor to form a dilute sodium carbonate liquor Na2CO3 (e.g. 700 ppm Na2CO3 to 300 ppm NaOH). The latter is then subjected to further filtration to remove impurity particulates then passed to reverse osmosis system. The low % liquor needs to be converted and concentrated to higher % sodium carbonate Na2CO3 liquor (e.g. 2400 ppm Na2CO3 to 1000 ppm NaOH) by passing it to a reverse osmosis system. Reverse osmosis (RO) unit contains RO cartridges cascaded with the C02-NaOH reactors in between. The objective is to keep the NaOH concentration below 300 ppm as the concentration of Na2CO3 is increased. That is, keep the pH-11. Kindly refer to figure3A, 3B and 3C showing mass balance analysis of the entire process (Pages 11,12,13). Flow chart of the ion exchange reverse osmosis system: Flow chart of the ion exchange reverse osmosis system (Kindly refer to figure 2 on page 10) Keep going until a 6% Na2CO3 solution (not soda ash powder) is obtained. At this point Na2CO3 solution (i.e. 6%) if evaporated by the available waste heat would produce dry soda ash. However, when 3.5% Na2CO3 is treated with Ca(OH)2 solution, we get: Na2CO3 + Ca(OH)2 -* 2NaOH + CaCO31 It is indicated in the worksheet that 24kg of Ca(OH)2 and -20 kg of NaCl are consumed to generate 13 kg of NaOH and 16 kg of CaCO3. In terms of effective evaporation, IMWH of thermal energy is required to produce one ton of dry NaOH. If the thermal energy is available as waste heat then we don't need to pay the I MWH penalty. From the WHQM process patent # PCT/1B2008/002020, waste heat that is provided by the solid waste processing unit can convert water into steam of 120 to 150 C having a boiler above the solid waste incinerator. The steam can be used to convert the 7% sodium hydroxide liquor to 50% liquor by evaporating half the volume or until it is dry sodium hydroxide. Ion exchangers that are used in this process are regenerated from either processed seawater or produced brine water. In the above schematic, if brine water concentration C is >10% salinity then the complex membrane and heat exchanger system is not needed. If brine water concentration 6% < C < 9% salinity then the complex membrane is not needed and the heat exchanger system can be used to raise its concentration to 10% or if it is cheaper NaCl is added to bring C up to 10%. If only seawater is available and the flue gas contains acidic gases such as hydrogen chloride and sulfur dioxide then these gases can be sparged with seawater under pressure to produce acidic sea water suitable for ion exchange processes. The acidic seawater can be used as a regenerent to eliminate the calcium and magnesium ions while sea water is used to wash the regenerated ion exchange and convert it to the Na+ form.
WO 2011/070384 PCT/IB2009/007713 4 One important aspect about this process is the circulation of RO permeate which save on pure water production and chemicals supply. There are waste products such as calcium chloride and magnesium chloride that can be diluted with the pure water produced from the complex membrane and heat exchanger system and returned back to the sea without harming the marine environment. The net production of potable water is difficult to estimate at this stage and depends on the government tolerance level of Ca++, Mg++ salts after dilution.
WO 2011/070384 PCT/IB2009/007713 5 Examples of intended use and other methods of industrial use The WHQM process is most convenient for industries that emit brine water (i.e. salinity between 6 to 16%) and lack any waste heat and C02 sources. However, it can also work on industries that emit a limited amount of C02 where the combined amounts from an industrial plant and the solid waste plant can be harnessed in C02 sequestration and caustic soda production. A solid waste process can operate on a large scale where solid waste incineration can be harnessed to generate C02, brine water, and heat for the WHQM process. The process can also accommodate flue gas emissions that contain acidic gases that can be harnessed in ion exchange regeneration. Several advantages gained include C02 and acidic gases (i.e. HCI & S02) sequestration. The former is known to cause global warming while the latter causes acid rain in far away regions.
Claims (14)
1. A process for producing a Na 2 CO 3 liquor containing at least 50wt% Na 2 CO 3 , the process including: contacting a solution of calcium hydroxide and sodium chloride with an ion exchange resin to form a caustic soda solution containing sodium chloride; sparging the caustic soda solution containing sodium chloride with carbon dioxide and an acidic gas containing HCL or H 2 SO 4 to form a Na 2 CO 3 solution containing sodium chloride; concentrating the Na 2 CO 3 solution containing sodium chloride through reverse osmosis to form the Na 2 CO 3 liquor containing at least 50up to about 6wt% Na 2 CO 3 ; using waste heat to further concentrate the Na 2 CO 3 liquor to a concentration of at least 50wt%.
2. The process of claim 1, further comprising the step of performing evaporation on the Na 2 CO 3 liquor to form solid Na 2 CO 3 .
3. The process of claim 1, further comprising the step of reacting the Na 2 CO 3 liquor with Ca(OH) 2 to form an NaOH liquor.
4. The process of claim 3, wherein the NaOH liquor is concentrated to 50wt% NaOH.
5. The process of claim 3, further comprising evaporating the NaOH liquor to form solid NaOH.
6. The process of claim 1, wherein the sodium chloride comes from sea water. 0
7. The process of any one of the preceding claims, wherein the carbon dioxide is provided from the combustion of waste solids.
8. The process of any one of the preceding claims, wherein the acidic gas is an acidic flue gas. 1000778158 7
9. The process of any one of the proceeding claims, wherein the ion exchange resin is a cation exchange resin, the process further including the step of regenerating the cation exchange resin.
10. The process of claim 9, wherein the cation exchange resin is regenerated using a regenerant selected from the group consisting of: water with a salinity of 6 to 12%, acidic water with an acidity of>8%.
11. The process of claim 10, wherein the regenerant is a NaCl solution.
12. The process of any one of the preceding claims, wherein the step of concentrating the Na 2 CO 3 solution includes multiple reverse osmosis stages.
13. The process of claim 1, wherein the step of concentrating the Na 2 CO 3 solution via reverse osmosis forms the Na 2 CO 3 liquor having about 6wt% Na 2 CO 3 .
14. The process of claim 2, wherein evaporation is performed using waste heat.
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
PCT/IB2009/007713 WO2011070384A1 (en) | 2009-12-09 | 2009-12-09 | Using the solid waste-quicklime membrane swqm process for the production of sodium hydroxide |
Publications (2)
Publication Number | Publication Date |
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AU2009356416A1 AU2009356416A1 (en) | 2012-07-26 |
AU2009356416B2 true AU2009356416B2 (en) | 2014-11-20 |
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AU2009356416A Ceased AU2009356416B2 (en) | 2009-12-09 | 2009-12-09 | Using the solid waste-quicklime membrane SWQM process for the production of sodium hydroxide |
Country Status (7)
Country | Link |
---|---|
US (1) | US20130272934A1 (en) |
EP (1) | EP2509919A1 (en) |
KR (1) | KR20120105504A (en) |
AP (1) | AP2012006365A0 (en) |
AU (1) | AU2009356416B2 (en) |
RU (1) | RU2538843C2 (en) |
WO (1) | WO2011070384A1 (en) |
Families Citing this family (1)
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CN103269769A (en) * | 2010-12-08 | 2013-08-28 | M·奥菲 | Using alkaline fly ash and similar byproducts in an ion-xchange/reverse osmosis process for the production of sodium carbonate |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2010010417A1 (en) * | 2008-07-23 | 2010-01-28 | Fze Engsl | A combined solid waste, carbon dioxide quicklime sparging, brine water, and reverse osmosis/ion exchange processes for the production of soda chemicals |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
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FR2729133A1 (en) * | 1995-01-11 | 1996-07-12 | Solvay | PROCESS FOR COPRODUCTION OF CALCIUM CARBONATE AND SODIUM HYDROXIDE |
AUPN105395A0 (en) * | 1995-02-10 | 1995-03-09 | Penrice Pty Ltd | Production of alkali metal bicarbonates and carbonates |
RU2274604C2 (en) * | 2004-07-19 | 2006-04-20 | Общество с ограниченной ответственностью Научно-технический центр "Химмодуль-XXI" (ООО НТЦ "Химмодуль-XXI") | Sodium hydroxide production process |
MX2010003363A (en) * | 2007-09-26 | 2010-09-07 | Bioteq Environmental Technolog | Selective sulphate removal by exclusive anion exchange from hard water waste streams. |
RU91530U1 (en) * | 2009-09-23 | 2010-02-20 | Закрытое акционерное общество Научно-производственное предприятие "Машпром" (ЗАО НПП "Машпром") | PLANT FOR PRODUCING CAUSTIC SODA FROM ELECTROLYTIC ALKALI |
-
2009
- 2009-12-09 AU AU2009356416A patent/AU2009356416B2/en not_active Ceased
- 2009-12-09 RU RU2012128544/05A patent/RU2538843C2/en not_active IP Right Cessation
- 2009-12-09 KR KR1020127017802A patent/KR20120105504A/en not_active Application Discontinuation
- 2009-12-09 US US13/521,127 patent/US20130272934A1/en not_active Abandoned
- 2009-12-09 AP AP2012006365A patent/AP2012006365A0/en unknown
- 2009-12-09 WO PCT/IB2009/007713 patent/WO2011070384A1/en active Application Filing
- 2009-12-09 EP EP09852000A patent/EP2509919A1/en not_active Withdrawn
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2010010417A1 (en) * | 2008-07-23 | 2010-01-28 | Fze Engsl | A combined solid waste, carbon dioxide quicklime sparging, brine water, and reverse osmosis/ion exchange processes for the production of soda chemicals |
Also Published As
Publication number | Publication date |
---|---|
EP2509919A1 (en) | 2012-10-17 |
RU2538843C2 (en) | 2015-01-10 |
RU2012128544A (en) | 2014-01-20 |
AP2012006365A0 (en) | 2012-08-31 |
AU2009356416A1 (en) | 2012-07-26 |
KR20120105504A (en) | 2012-09-25 |
US20130272934A1 (en) | 2013-10-17 |
WO2011070384A1 (en) | 2011-06-16 |
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