US20130272934A1 - 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 PDF

Info

Publication number
US20130272934A1
US20130272934A1 US13/521,127 US200913521127A US2013272934A1 US 20130272934 A1 US20130272934 A1 US 20130272934A1 US 200913521127 A US200913521127 A US 200913521127A US 2013272934 A1 US2013272934 A1 US 2013272934A1
Authority
US
United States
Prior art keywords
liquor
naoh
na2co3
produce
acidic
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.)
Abandoned
Application number
US13/521,127
Inventor
Mohammed Olfi
Tarek R. Farhat
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Publication of US20130272934A1 publication Critical patent/US20130272934A1/en
Abandoned legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/10Obtaining alkali metals
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D1/00Oxides or hydroxides of sodium, potassium or alkali metals in general
    • C01D1/04Hydroxides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D1/00Oxides or hydroxides of sodium, potassium or alkali metals in general
    • C01D1/04Hydroxides
    • C01D1/20Preparation by reacting oxides or hydroxides with alkali metal salts
    • C01D1/22Preparation by reacting oxides or hydroxides with alkali metal salts with carbonates or bicarbonates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D7/00Carbonates of sodium, potassium or alkali metals in general
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D7/00Carbonates of sodium, potassium or alkali metals in general
    • C01D7/07Preparation from the hydroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Definitions

  • the present invention uses a classical equation where CO2 is reacted with caustic soda NaOH to produce clear solution of sodium carbonate Na2CO3 such that:
  • regenerants such as brine water with a salinity of 6 to 12%, acidic water with acidity of >8% (e.g. HCl or H2SO4) or a combination of both is crucial because it is used to regenerate the cation exchanger such that:
  • One aspect of the present patent requires a sparging reactor to bubble acidic flue gas where gases such as HCl and SO2 can be captured to produce acidic solutions such that,
  • 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 1 MW is required to produce one ton of solid product.
  • the most obvious heat source is the heat emitted by solid waste incineration or any other waste heal source.
  • Solid waste, brine water waste, and CO2 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.
  • 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.
  • the only byproduct is CaCO3 while in chloro-alkali technology dangerous gases such as chlorine and hydrogen have to be handled safely.
  • 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.
  • RO unit contains RO cartridges cascaded with the CO2-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.
  • FIGS. 3A , 3 B and 3 C showing mass balance analysis of the entire process (Pages 11,12,13).
  • 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.
  • 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 Cup to 10%.
  • 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.
  • 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 CO2 sources. However, it can also work on industries that emit a limited amount of CO2 where the combined amounts from an industrial plant and the solid waste plant can be harnessed in CO2 sequestration and caustic soda production.
  • a solid waste process can operate on a large scale where solid waste incineration can be harnessed to generate CO2, 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.
  • CO2 and acidic gases i.e. HCl & SO2
  • the former is known to cause global warming while the latter causes acid rain in far away regions.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Mechanical Engineering (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Manufacturing & Machinery (AREA)
  • Metallurgy (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Treating Waste Gases (AREA)
  • Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)

Abstract

The proposed invention uses ion exchange technology to produce dilute caustic soda liquor from calcium hydroxide liquor Ca(OH)2 followed by the reaction of carbon dioxide CO2 with caustic soda to produce dilute sodium carbonate solution. Multiple reverse osmosis and acidic CO2 sparging can concentrate the Na2CO3 liquor to 6-7%. The 6-7% liquor is treated with waste heat to produce 50% or solid Na2CO3. 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 output of many industrial processes generates waste heat, brine water and CO2 and the present invention combines these components in the production of solid Na2CO3, NaOH or their high % liquors. Availability of waste heat sources can lead to higher efficiency in Na2CO3 and NaOH production. The process is not electrochemical chloro alkali technology or Solvay process.

Description

    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 CO2 is reacted with caustic soda NaOH to produce clear solution of sodium carbonate Na2CO3 such that:

  • NaOH+CO2→Na2CO3
  • Presence of regenerants such as brine water with a salinity of 6 to 12%, acidic water with acidity of >8% (e.g. HCl 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++CaCl2
  • (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 HCl and SO2 can be captured to produce acidic solutions such that,
  • HCl(g)+H2O→HCl(aq) used for strong ion exchange regeneration
  • SO2(g)+H2O+O→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 1 MW 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 heal source.
  • Description of how the invention addresses a technical problem
  • Solid waste, brine water waste, and CO2 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 CaCO3 while in chloro-alkali technology dangerous gases such as chlorine and hydrogen have to be handled safely.
  • 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 FIG. 1 on 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 CO2-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 FIGS. 3A, 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 FIG. 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+CaCO3↓
  • It is indicated in the worksheet that 24 kg 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, 1 MWH 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 1 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 Cup 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.
  • 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.
  • 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 CO2 sources. However, it can also work on industries that emit a limited amount of CO2 where the combined amounts from an industrial plant and the solid waste plant can be harnessed in CO2 sequestration and caustic soda production. A solid waste process can operate on a large scale where solid waste incineration can be harnessed to generate CO2, 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 CO2 and acidic gases (i.e. HCl & SO2) sequestration. The former is known to cause global warming while the latter causes acid rain in far away regions.

Claims (5)

1. 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 CO2 with caustic soda to produce dilute sodium carbonate solution. Multiple reverse osmosis and acidic CO2 sparging can concentrate the Na2CO3 liquor to 6-7%. The 6-7% liquor is treated with waste heat to produce 50% or solid Na2CO3. 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 CO2, Ca(OH)2, and sodium chloride NaCl to produce NaOH. The output of many industrial processes generates waste heat, brine water, and CO2 and the present invention combines these components in the production of solid Na2CO3, NaOH or their high % liquors. Availability of waste heat sources can lead to higher efficiency in Na2CO3 and NaOH production. The process is not electrochemical chloro-alkali technology or Solvay process. There 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.
2. 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.
3. The use of brine and acidic water and advanced membrane and resin technology in solid waste processing and the production of soda ash Na2CO3 and caustic soda NaOH.
4. The process by which this invention attempts to bring solid waste, brine water waste, acidic water waste extracted from acidic flue gas, and CO2 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.
5. The process which essentially relies on advanced membrane technology systems to produce soda ash Na2CO3 and caustic soda NaOH we claim the following combined stages (i) to (iv) of the process:
(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 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 under controlled pH conditions.
(iv)-Reverse osmosis (RO) unit contains RO cartridges cascaded with the CO2-NaOH reactors in between. The objective is to keep the NaOH concentration below 300 ppm as the concentration of Na2CO3 is increased.
US13/521,127 2009-12-09 2009-12-09 Using the solid waste-quicklime membrane swqm process for the production of sodium hydroxide Abandoned US20130272934A1 (en)

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 (1)

Publication Number Publication Date
US20130272934A1 true US20130272934A1 (en) 2013-10-17

Family

ID=44145144

Family Applications (1)

Application Number Title Priority Date Filing Date
US13/521,127 Abandoned US20130272934A1 (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)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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
US8551340B2 (en) * 2007-09-26 2013-10-08 Bioteq Environmental Technologies Inc. Method for selective sulphate removal by exclusive anion exchange from hard water waste streams
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
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

Also Published As

Publication number Publication date
EP2509919A1 (en) 2012-10-17
WO2011070384A1 (en) 2011-06-16
RU2538843C2 (en) 2015-01-10
RU2012128544A (en) 2014-01-20
AU2009356416A1 (en) 2012-07-26
AU2009356416B2 (en) 2014-11-20
AP2012006365A0 (en) 2012-08-31
KR20120105504A (en) 2012-09-25

Similar Documents

Publication Publication Date Title
US8623316B2 (en) Combined solid waste, carbon dioxide quicklime sparging, brine water, and reverse osmosis/ion exchange processes for the production of soda chemicals
US11235281B2 (en) Multi-pollutant exhaust treatment using seawater for marine applications
US20130323143A1 (en) Using alkaline fly ash and similar byproducts in an ion-exchange/reverse osmosis process for the production of sodium carbonate
EP3895785A1 (en) Unit for desalination and greenhouse gas sequestration
US10052584B2 (en) Water recycling in a CO2 removal process and system
CA3108086A1 (en) Processing of lithium containing brines
WO2013016708A1 (en) Electrochemical desalination cell
Tu et al. Reclaimed seawater discharge–desalination brine treatment and resource recovery system
AU2009356416B2 (en) Using the solid waste-quicklime membrane SWQM process for the production of sodium hydroxide
Davies Solar thermal decomposition of desalination reject brine for carbon dioxide removal and neutralisation of ocean acidity
CN112437754B (en) Method for removing contaminants from wastewater from an industrial plant and system for implementing such a method
US20240166543A1 (en) Methods of seawater softening for desalination and mineral extraction
US20180079667A1 (en) Process for the treatment of water
US20230382754A1 (en) Simultaneous CO2 Capture, Mineralization, and Lithium and Other Metal Extraction from Brine
WO2023136778A1 (en) Method and apparatus for removing a target substance from a gas
US12030016B2 (en) Systems and methods for direct air carbon dioxide capture
US20240238721A1 (en) Systems and methods for direct air carbon dioxide capture
US20230191322A1 (en) Systems and methods for direct air carbon dioxide capture
WO2024080132A1 (en) Method for fixing carbon dioxide
De et al. Sea Water-The Source of Solutions of Modern-Day Water and Other crucial Crisis
WO2013117950A1 (en) A combined reverse osmosis/ion exchange/electrodialysis (croied) process that uses gypsum as a raw material to produce sulfuric acid and sodium hydroxide

Legal Events

Date Code Title Description
STCB Information on status: application discontinuation

Free format text: ABANDONED -- FAILURE TO RESPOND TO AN OFFICE ACTION