WO2011115636A1 - Systems and processes for treatment of solutions - Google Patents

Systems and processes for treatment of solutions Download PDF

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Publication number
WO2011115636A1
WO2011115636A1 PCT/US2010/040877 US2010040877W WO2011115636A1 WO 2011115636 A1 WO2011115636 A1 WO 2011115636A1 US 2010040877 W US2010040877 W US 2010040877W WO 2011115636 A1 WO2011115636 A1 WO 2011115636A1
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WIPO (PCT)
Prior art keywords
organic solvents
devices
liquid
unit
aqueous phase
Prior art date
Application number
PCT/US2010/040877
Other languages
French (fr)
Inventor
Jiyang Xia
Rihua Xiong
Wei Cai
Wenqing Peng
Zijun Xia
Yiwen Sun
Original Assignee
General Electric Company
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.)
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Publication date
Application filed by General Electric Company filed Critical General Electric Company
Priority to BR112012021755A priority Critical patent/BR112012021755A2/en
Priority to US13/062,857 priority patent/US9828270B2/en
Priority to EP10731883A priority patent/EP2547628A1/en
Priority to SG2012067112A priority patent/SG183998A1/en
Publication of WO2011115636A1 publication Critical patent/WO2011115636A1/en

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D11/00Solvent extraction
    • B01D11/04Solvent extraction of solutions which are liquid
    • B01D11/0488Flow sheets
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D11/00Solvent extraction
    • B01D11/04Solvent extraction of solutions which are liquid
    • B01D11/0492Applications, solvents used
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/02Reverse osmosis; Hyperfiltration ; Nanofiltration
    • B01D61/10Accessories; Auxiliary operations
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14Ultrafiltration; Microfiltration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D61/00Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/58Multistep processes
    • 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
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • 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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • 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
    • C02F1/38Treatment of water, waste water, or sewage by centrifugal separation
    • 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
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/469Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • 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
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/08Seawater, e.g. for desalination

Definitions

  • This invention relates generally to systems and processes for treatment of solutions. More particularly, the invention relates to systems and processes for treatment of aqueous saline solutions using miscible organic solvents.
  • a treatment system is provided in accordance with one embodiment of the invention.
  • the treatment system comprises a precipitation unit and a recovery unit.
  • the precipitation unit is configured to treat a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid.
  • the recovery unit is in fluid communication with the precipitation unit and configured to facilitate separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents.
  • the treatment system further comprises a purification unit comprising one or more membrane devices in fluid communication with the recovery unit and configured to separate at least a portion of the one or more miscible organic solvents in the aqueous phase liquid from the aqueous phase liquid.
  • a treatment system is provided in accordance with another embodiment of the invention.
  • the treatment system comprises a precipitation unit and a recovery unit.
  • the precipitation unit is configured to treat a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid.
  • the recovery unit is in fluid communication with the precipitation unit and configured to facilitate separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents.
  • the treatment system further comprises a removal device comprising an ionization source and a purification unit in fluid communication with the recovery unit.
  • the ionization source is configured to provide one or more ionization materials to ionize at least a portion of the one or more organic solvents in the aqueous phase liquid.
  • the removal device is configured to receive the aqueous phase liquid to separate at least a portion of the one or more ionized miscible organic solvents from the aqueous phase liquid.
  • Another aspect of the invention further comprises a treatment process.
  • the treatment process comprises treating a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid, separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents, and introducing the aqueous liquid into one or more of one or more membrane devices and one or more ion removal devices to separate at least a portion of the one or more miscible organic solvents in the aqueous phase liquid from the aqueous phase liquid.
  • FIG. 1 is a schematic diagram of a treatment system for treating solutions in accordance with one embodiment of the invention.
  • FIG. 2 is a schematic flow chart of a treatment process in accordance with one embodiment of the invention.
  • FIG. 1 is a schematic diagram of a treatment system 10 for treating a solution 17.
  • the solution 17 may comprise any saline solution or water.
  • the saline solution may comprise, but not limited to, any liquid having a salt content of at least about 2000 ppm of total dissolved salts (TDS).
  • TDS total dissolved salts
  • the saline solution may comprise, but not limited to, any liquid having a salt content larger than about 10,000 ppm TDS.
  • the saline water comprises fracturing water.
  • the treatment system 10 is configured to perform the treatment, such as precipitation of salt species in the solution 17 via using one or more miscible organic solvents to reduce concentrations of the salt species to produce product water.
  • miscible organic solvent is not limited to any particular miscible organic solvent, and may be selected based on different applications.
  • the miscible organic solvent may comprise amine.
  • the amine has the formula (a):
  • the miscible organic solvent may have the formula (b):
  • Rl, R2 and R3 may be same or different and may be independently selected from the group consisting of saturated or unsaturated, branched or unbranched, substituted or unsubstituted, linear or cyclic CI -CI 4 hydrocarbons including or not including heteroatoms.
  • one or more of Rl, R2 and R3 may comprise methyl, ethyl, n-propyl, isopropyl, n-butyl, isobutyl, 2-methylhexyl, octyl, benzyl and phenyl.
  • the miscible organic solvent may include isopropylamine, propylamine, acetone, methanol, ethanol, acetonitrile, diisopropylamine, tetrahydrofuran, dioxane, tetrahydropyrimidine (THP), N-methyltetrahydropyrimidine (MTHP) and combinations thereof.
  • the miscible organic solvent comprises diisopropylamine.
  • salts selected from the group consisting of halides of sodium, calcium, barium, strontium, and radium, bicarbonates of sodium, potassium, magnesium, calcium, barium, strontium, and radium, silicates of sodium, potassium, magnesium, and radium, selenites, selenates, selenides of sodium, potassium, magnesium, calcium, barium, strontium, and radium, selenide salts selected from the group consisting of phosphorous sub-selenide, phosphorous monoselenide, phosphorous tri-selenide, and phosphorous penta-selenide, selenium halide salts selected from the group consisting of selenium mono-chloride, selenium tetra-chloride, selenium mono-bromide, and selenium tetra-bromide, phosphates of sodium, potassium, magnesium, calcium, barium, strontium, and radium, boron salts of sodium, potassium, magnesium, calcium,
  • the treatment system 10 comprises a precipitation unit 11, a solid-liquid separation unit 12, a recovery unit 13 and a purification unit 14.
  • the precipitation unit 11 comprises an organic solvent source 15 and a precipitation device 16.
  • the organic solvent source 15 is configured to provide the miscible organic solvent.
  • the precipitation device 16 may comprise a vessel and is configured to accommodate the solution 17 from a solution source (not shown) and the miscible organic solvent from the organic solvent source 15.
  • the solution 17 and the miscible organic solvent may be mixed with each other within the precipitation device 16, so that one or more of the salt species in the solution 17 precipitate to form a mixture of precipitate solids 18 and a liquid 19.
  • the solid-liquid separation unit 12 is in fluid communication with the precipitation unit 11 for receiving and separating the precipitate solids 18 and a portion of the liquid 19.
  • the solid-liquid separation unit 12 is not limited to any particular device suitable for separation of the precipitate solids 18 and the portion of the liquid 19.
  • Non-limiting examples of the solid-liquid separation unit 12 include one or more hydrocyclones, one or more centrifuges, one or more filter presses, one or more cartridge filters, one or more vacuum filtration devices, and one or more microfiltration devices.
  • the solid-liquid separation unit 12 may comprise one or more hydrocyclones serially connected to each other.
  • the precipitate solids 18 may be removed from the portion of the liquid 19.
  • the recovery unit 13 is in fluid communication with and receives the liquid 19 from the solid-liquid separation unit 12 and an upper portion (not labeled) of the precipitation device 16.
  • the recovery unit 13 is configured to facilitate separation of the liquid 19, for example, to separate a liquid with different phases.
  • the recovery unit 13 may comprise a vessel, in which the separation of the liquid 19 occurs.
  • the liquid 19 is heated and at least separated into an aqueous phase liquid 20 and an organic phase liquid 21 in the recovery unit 13.
  • the recovery unit 13 may comprise one or more membrane distillation devices for separation, so that the organic phase liquid 21 is separated from the aqueous phase liquid 20 and recovered.
  • the recovered miscible organic solvent may be reintroduced into the precipitation device 16 for facilitating the precipitation of the salt species in other solutions.
  • the aqueous phase liquid 20 from the recovery unit 13 may be introduced into the purification unit 14 for the separation of at least a portion of the residual miscible organic solvent from the aqueous phase liquid 20.
  • the purification unit 14 comprises a removal device 23.
  • the removal device 23 may comprise any devices suitable for the separation of the residual miscible organic solvent from the aqueous phase liquid 20.
  • the removal device 23 may comprise one or more membrane devices employing one or more membranes to remove the residual organic solvent.
  • Non-limiting examples of the one or more membrane devices may comprise one or more of one or more reverse osmosis devices, one or more nanofiltration devices, and one or more membrane distillation devices.
  • a fluid 22 comprising at least a portion of the residual organic solvent may be removed from the aqueous phase liquid 20, and a product liquid 24 may be produced.
  • the removal device 23 may comprise one or more ion removal devices including, but not limited to one or more ion exchange resins, one or more reverse osmosis devices, one or more electrodialysis reversal devices, one or more membrane distillation devices, and one or more supercapacitor desalination devices.
  • the purification unit 14 may further comprise an ionization source 25 disposed upstream from and in fluid communication with the removal device 23 for providing one or more ionization materials to ionize the residual miscible organic solvent in the aqueous phase fluid 20.
  • the one or more ionization materials may comprise one or more pH adjustment materials.
  • the one or more pH adjustment materials may be introduced to adjust the pH values of the aqueous phase liquid 20 so as to ionize at least a portion of the residual organic solvent for facilitating the separation.
  • the pH values of the aqueous phase liquid 20 may be reduced.
  • the one or more pH adjustment materials may comprise one or more acids.
  • Non-limiting examples of the one or more acids may comprise hydrochloric acids, sulphuric acids and other suitable acids.
  • the removed residual miscible organic solvent may also be reintroduced into the precipitation unit 11.
  • the salt species and the miscible organic solvents may be removed from the solutions 17 respectively, so that the product liquid 24 is produced with high efficiency and low energy consumption.
  • the treatment system 10 may comprise a pretreatment unit 26 disposed upstream from and in fluid communication with the precipitation device 16.
  • the pretreatment unit 26 may comprise a vessel and accommodate one or more pretreatment materials.
  • the pretreatment materials in the pretreatment unit 26 may mix with the solution 17 to reduce the concentration of one or more ion species before the solution 17 is introduced into the precipitation unit 11.
  • a pretreatment source (not shown) may be provided separately from and provide the one or more pretreatment materials into the pretreatment unit 26.
  • the one or more pretreatment materials may not be limited to any particular pretreatment materials, and may be selected based on different ion species in the solution 17.
  • the one or more pretreatment materials comprise one or more soluble materials having sulfate radical anions, for example sulphuric acid, so as to remove cations, such as barium cations and/or selenium cations in the solution 17 in the form of precipitates.
  • the treatment system 10 may further comprise one or more heat-exchanging apparatuses 27 disposed between the pretreatment unit 26 and the precipitation unit 11, between the solid-liquid separation unit 12 and the recovery unit 13, and/or between the recovery unit 13 and the purification unit 14 for thermal exchange.
  • the recovery unit 13 may be integrated with a heat-exchanging apparatus including, but not limited to a heater.
  • FIG. 1 is merely illustrative.
  • the precipitation device 16 and the solid- liquid separation unit 12 are provided separately.
  • the precipitation device 16 and the solid-liquid separation unit 13 may be integrated to act as one element for performing the precipitation and the separation.
  • the pretreatment unit 26 and/or the solid-liquid separation unit 12 may not be employed.
  • the solution 17 may be directly introduced into the precipitation unit 11, so that the liquid 19 at the upper portion of the precipitation device 16 may be introduced into the recovery unit 13 after the salt species precipitate to settle down at a lower portion of the precipitation device 16.
  • FIG. 2 is a schematic flow chart of a treatment process 30.
  • a certain amount of the solution 17 and a certain amount of the pretreatment material are introduced into the pretreatment unit 26 to remove one or more ion species.
  • the solutions 17 are then delivered into the precipitation unit 11.
  • a certain amount of the miscible organic solvent from the organic solvent source 15 are also introduced into the precipitation device 16 to mix with the solution 17, so that one or more salt species precipitate from the solutions 17 due to their lower solubility in the miscible organic solvent and form the mixture of the precipitate solids 18 and the liquid 19.
  • step 33 the precipitate solids 18 and a portion of the liquid 19 is introduced into the solid-liquid separation unit 12 for separation.
  • step 34 after the separation of the precipitate solids 18 from the portion of the liquid 19, the liquid 19 from the precipitation unit 11 and the solid-liquid separation unit 12 is introduced into the recovery unit 13.
  • the liquid 19 may be heated to a higher temperature, so that the miscible organic solvent 21 is separated from the liquid 19 within the recovery unit 13 in the form of layers of the organic phase liquid 21 and the aqueous phase liquid 20.
  • the aqueous phase liquid 20 is introduced into the purification unit 14 for separation of the residual miscible organic solvent 22 from the aqueous phase liquid 20.
  • a certain amount of the pH adjustment material may be mixed with and adjust the pH values of the aqueous phase liquid 20 from the recovery unit 13 so as to ionize the residual miscible organic solvent 22, so that the residual miscible organic solvent 22 is separated and recovered after passing through the purification unit 14.
  • the adjusted pH values of the aqueous phase liquid 20 may be about 4-5.
  • step 34 and/or the recovered residual miscible organic solvents 22 in step 35 may be reintroduced into the precipitation device 16.
  • one or more heat exchanging steps may be employed before the precipitation step 32, the solid-liquid separation step 33, the liquid-liquid separation step 34 and/or the recovery step 35.
  • the solutions 17 prior to the precipitation step 32, the solutions 17 may be cooled, for example, to about 0°C for the subsequent precipitation step 32.
  • the liquid-liquid separation step 34 may be performed at a higher temperature, such as about 70°C.
  • the aqueous phase liquid 20 from the recovery unit 13 Prior to the step 35, the aqueous phase liquid 20 from the recovery unit 13 may also be cooled, for example, to about 25° C for the recovery step 35. Additionally, in certain applications, the pretreatment step 31 and/or the solid-liquid separation step 33 may not be employed.
  • the salt species due to the presence of the miscible organic solvent in the solution, the salt species may be removed with lower cost and higher efficiency.
  • the residual miscible organic solvent may be readily removed with lower energy consumption via adjustment of the pH values of the aqueous phase liquid so as to produce the product liquid.

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

A treatment system is provided and comprises a precipitation unit and a recovery unit. The precipitation unit is configured to treat a solution using one or more miscibie organic solvents to produce a mixture of precipitate solids and a liquid. The recov ery unit is in fluid communication with the precipitation unit and configured to facilitate separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents. The treatment system further comprises a purification unit comprising one or more membrane devices in fluid communication with the recovery unit and configured to separate at least a portion of the one or more miscible organic solvents in the aqueous phase liquid from the aqueous phase liquid. A treatment system and a treatment process are also presented.

Description

SYSTEMS AND PROCESSES FOR TREATMENT OF SOLUTIONS
BACKGROUND
[0001] This invention relates generally to systems and processes for treatment of solutions. More particularly, the invention relates to systems and processes for treatment of aqueous saline solutions using miscible organic solvents.
[0002] In industrial processes, large amounts of solutions, such as saline solutions are produced. Generally, such aqueous saline solutions are not suitable for direct consumption in domestic or industrial applications. In view of the limited eligible water sources and protection of environment, some treatment processes, such as de-ionization and desaltification for treatment of wastewater, seawater or brackish water, become options to produce eligible water.
[0003] In current applications, various treatment processes, such as distillation, vaporization and chemical precipitation are employed for treatment of solutions. However, such processes can suffer from low efficiency and/or high- energy consumption, for example, for directly treating high saline solutions, such as fracturing water, which may prohibit them from being widely implemented.
[0004] Therefore, there is a need for new and improved systems and methods for treatment of aqueous saline solutions, such as fracturing water.
BRIEF DESCRIPTION
[0005] A treatment system is provided in accordance with one embodiment of the invention. The treatment system comprises a precipitation unit and a recovery unit. The precipitation unit is configured to treat a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid. The recovery unit is in fluid communication with the precipitation unit and configured to facilitate separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents. The treatment system further comprises a purification unit comprising one or more membrane devices in fluid communication with the recovery unit and configured to separate at least a portion of the one or more miscible organic solvents in the aqueous phase liquid from the aqueous phase liquid.
[0006] A treatment system is provided in accordance with another embodiment of the invention. The treatment system comprises a precipitation unit and a recovery unit. The precipitation unit is configured to treat a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid. The recovery unit is in fluid communication with the precipitation unit and configured to facilitate separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents. The treatment system further comprises a removal device comprising an ionization source and a purification unit in fluid communication with the recovery unit. The ionization source is configured to provide one or more ionization materials to ionize at least a portion of the one or more organic solvents in the aqueous phase liquid. The removal device is configured to receive the aqueous phase liquid to separate at least a portion of the one or more ionized miscible organic solvents from the aqueous phase liquid.
[0007] Another aspect of the invention further comprises a treatment process.
The treatment process comprises treating a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid, separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents, and introducing the aqueous liquid into one or more of one or more membrane devices and one or more ion removal devices to separate at least a portion of the one or more miscible organic solvents in the aqueous phase liquid from the aqueous phase liquid.
BRIEF DESCRIPTION OF THE DRAWINGS
[0008] The above and other aspects, features, and advantages of the present disclosure will become more apparent in light of the subsequent detailed description when taken in conjunction with the accompanying drawings in which: [0009] FIG. 1 is a schematic diagram of a treatment system for treating solutions in accordance with one embodiment of the invention; and
[0010] FIG. 2 is a schematic flow chart of a treatment process in accordance with one embodiment of the invention.
DETAILED DESCRIPTION OF THE INVENTION
[0011] Embodiments of the present disclosure are described herein with reference to the accompanying drawings. In the subsequent description, well-known functions or constructions are not described in detail to avoid obscuring the disclosure in unnecessary detail. As used herein, the singular forms "a," "an" and "the" include plural referents unless the context clearly dictates otherwise.
[0012] FIG. 1 is a schematic diagram of a treatment system 10 for treating a solution 17. In non-limiting examples, the solution 17 may comprise any saline solution or water. In some applications, the saline solution may comprise, but not limited to, any liquid having a salt content of at least about 2000 ppm of total dissolved salts (TDS). In other applications, the saline solution may comprise, but not limited to, any liquid having a salt content larger than about 10,000 ppm TDS. In one non-limiting example, the saline water comprises fracturing water.
[0013] In embodiments of the invention, the treatment system 10 is configured to perform the treatment, such as precipitation of salt species in the solution 17 via using one or more miscible organic solvents to reduce concentrations of the salt species to produce product water. It should be noted that the miscible organic solvent is not limited to any particular miscible organic solvent, and may be selected based on different applications.
[0014] In some applications, the miscible organic solvent may comprise amine.
In one example, the amine has the formula (a):
Figure imgf000005_0001
Alternatively, the miscible organic solvent may have the formula (b):
Figure imgf000006_0001
In the formulas (a) and (b), wherein Rl, R2 and R3 may be same or different and may be independently selected from the group consisting of saturated or unsaturated, branched or unbranched, substituted or unsubstituted, linear or cyclic CI -CI 4 hydrocarbons including or not including heteroatoms.
[0015] In some examples, one or more of Rl, R2 and R3 may comprise methyl, ethyl, n-propyl, isopropyl, n-butyl, isobutyl, 2-methylhexyl, octyl, benzyl and phenyl. The miscible organic solvent may include isopropylamine, propylamine, acetone, methanol, ethanol, acetonitrile, diisopropylamine, tetrahydrofuran, dioxane, tetrahydropyrimidine (THP), N-methyltetrahydropyrimidine (MTHP) and combinations thereof. In one example, the miscible organic solvent comprises diisopropylamine.
[0016] Additionally, non-limiting examples of the salt species in the solution
17 include salts selected from the group consisting of halides of sodium, calcium, barium, strontium, and radium, bicarbonates of sodium, potassium, magnesium, calcium, barium, strontium, and radium, silicates of sodium, potassium, magnesium, and radium, selenites, selenates, selenides of sodium, potassium, magnesium, calcium, barium, strontium, and radium, selenide salts selected from the group consisting of phosphorous sub-selenide, phosphorous monoselenide, phosphorous tri-selenide, and phosphorous penta-selenide, selenium halide salts selected from the group consisting of selenium mono-chloride, selenium tetra-chloride, selenium mono-bromide, and selenium tetra-bromide, phosphates of sodium, potassium, magnesium, calcium, barium, strontium, and radium, boron salts of sodium, potassium, magnesium, calcium, barium, strontium, and radium, sulfate salts of sodium, potassium and radium, carbonate salts of sodium, potassium and magnesium, and combinations thereof.
[0017] As illustrated in FIG. 1, the treatment system 10 comprises a precipitation unit 11, a solid-liquid separation unit 12, a recovery unit 13 and a purification unit 14. The precipitation unit 11 comprises an organic solvent source 15 and a precipitation device 16. In some embodiments, the organic solvent source 15 is configured to provide the miscible organic solvent. The precipitation device 16 may comprise a vessel and is configured to accommodate the solution 17 from a solution source (not shown) and the miscible organic solvent from the organic solvent source 15. The solution 17 and the miscible organic solvent may be mixed with each other within the precipitation device 16, so that one or more of the salt species in the solution 17 precipitate to form a mixture of precipitate solids 18 and a liquid 19.
[0018] The solid-liquid separation unit 12 is in fluid communication with the precipitation unit 11 for receiving and separating the precipitate solids 18 and a portion of the liquid 19. The solid-liquid separation unit 12 is not limited to any particular device suitable for separation of the precipitate solids 18 and the portion of the liquid 19. Non-limiting examples of the solid-liquid separation unit 12 include one or more hydrocyclones, one or more centrifuges, one or more filter presses, one or more cartridge filters, one or more vacuum filtration devices, and one or more microfiltration devices.
[0019] In some applications, the solid-liquid separation unit 12 may comprise one or more hydrocyclones serially connected to each other. When the mixture of the precipitate solids 18 and the portion of the liquid 19 from the precipitation unit 11 is introduced into the solid-liquid separation unit 12, the precipitate solids 18 may be removed from the portion of the liquid 19.
[0020] For the arrangement illustrated in FIG. 1, the recovery unit 13 is in fluid communication with and receives the liquid 19 from the solid-liquid separation unit 12 and an upper portion (not labeled) of the precipitation device 16. The recovery unit 13 is configured to facilitate separation of the liquid 19, for example, to separate a liquid with different phases. [0021] In some examples, the recovery unit 13 may comprise a vessel, in which the separation of the liquid 19 occurs. For example, the liquid 19 is heated and at least separated into an aqueous phase liquid 20 and an organic phase liquid 21 in the recovery unit 13. In other examples, the recovery unit 13 may comprise one or more membrane distillation devices for separation, so that the organic phase liquid 21 is separated from the aqueous phase liquid 20 and recovered. In some applications, the recovered miscible organic solvent may be reintroduced into the precipitation device 16 for facilitating the precipitation of the salt species in other solutions.
[0022] In certain applications, after the separation in the recovery unit 13, a portion of the miscible organic solvent is removed from the liquid 19. A certain amount of residual miscible organic solvent may still remain in the aqueous phase liquid 20. Accordingly, the aqueous phase liquid 20 from the recovery unit 13 may be introduced into the purification unit 14 for the separation of at least a portion of the residual miscible organic solvent from the aqueous phase liquid 20.
[0023] In the illustrated example, the purification unit 14 comprises a removal device 23. The removal device 23 may comprise any devices suitable for the separation of the residual miscible organic solvent from the aqueous phase liquid 20. In some examples, the removal device 23 may comprise one or more membrane devices employing one or more membranes to remove the residual organic solvent. Non-limiting examples of the one or more membrane devices may comprise one or more of one or more reverse osmosis devices, one or more nanofiltration devices, and one or more membrane distillation devices.
[0024] Thus, a fluid 22 comprising at least a portion of the residual organic solvent may be removed from the aqueous phase liquid 20, and a product liquid 24 may be produced. Alternatively, the removal device 23 may comprise one or more ion removal devices including, but not limited to one or more ion exchange resins, one or more reverse osmosis devices, one or more electrodialysis reversal devices, one or more membrane distillation devices, and one or more supercapacitor desalination devices. [0025] In certain applications, the purification unit 14 may further comprise an ionization source 25 disposed upstream from and in fluid communication with the removal device 23 for providing one or more ionization materials to ionize the residual miscible organic solvent in the aqueous phase fluid 20. In non-limiting examples, the one or more ionization materials may comprise one or more pH adjustment materials. As a result, before the separation of the residual organic solvent in the removal device 23, the one or more pH adjustment materials may be introduced to adjust the pH values of the aqueous phase liquid 20 so as to ionize at least a portion of the residual organic solvent for facilitating the separation.
[0026] In some examples, the pH values of the aqueous phase liquid 20 may be reduced. The one or more pH adjustment materials may comprise one or more acids. Non-limiting examples of the one or more acids may comprise hydrochloric acids, sulphuric acids and other suitable acids. In certain applications, the removed residual miscible organic solvent may also be reintroduced into the precipitation unit 11.
[0027] Accordingly, due to the miscible organic solvents and the pH adjustment materials, the salt species and the miscible organic solvents may be removed from the solutions 17 respectively, so that the product liquid 24 is produced with high efficiency and low energy consumption.
[0028] For the arrangement illustrated in FIG. 1, in some embodiments, the treatment system 10 may comprise a pretreatment unit 26 disposed upstream from and in fluid communication with the precipitation device 16. In some examples, the pretreatment unit 26 may comprise a vessel and accommodate one or more pretreatment materials. When the solution 17 is introduced into the pretreatment unit 26, the one or more pretreatment materials in the pretreatment unit 26 may mix with the solution 17 to reduce the concentration of one or more ion species before the solution 17 is introduced into the precipitation unit 11. Additionally, a pretreatment source (not shown) may be provided separately from and provide the one or more pretreatment materials into the pretreatment unit 26. [0029] In some embodiments, the one or more pretreatment materials may not be limited to any particular pretreatment materials, and may be selected based on different ion species in the solution 17. For example, the one or more pretreatment materials comprise one or more soluble materials having sulfate radical anions, for example sulphuric acid, so as to remove cations, such as barium cations and/or selenium cations in the solution 17 in the form of precipitates.
[0030] In certain applications, the treatment system 10 may further comprise one or more heat-exchanging apparatuses 27 disposed between the pretreatment unit 26 and the precipitation unit 11, between the solid-liquid separation unit 12 and the recovery unit 13, and/or between the recovery unit 13 and the purification unit 14 for thermal exchange. In some applications, the recovery unit 13 may be integrated with a heat-exchanging apparatus including, but not limited to a heater.
[0031] It should be noted that the arrangement shown in FIG. 1 is merely illustrative. For the illustrated embodiment, the precipitation device 16 and the solid- liquid separation unit 12 are provided separately. Alternatively, the precipitation device 16 and the solid-liquid separation unit 13 may be integrated to act as one element for performing the precipitation and the separation.
[0032] In other examples, the pretreatment unit 26 and/or the solid-liquid separation unit 12 may not be employed. The solution 17 may be directly introduced into the precipitation unit 11, so that the liquid 19 at the upper portion of the precipitation device 16 may be introduced into the recovery unit 13 after the salt species precipitate to settle down at a lower portion of the precipitation device 16.
[0033] FIG. 2 is a schematic flow chart of a treatment process 30. As illustrated in FIGS. 1-2, during the treatment process, in step 31, a certain amount of the solution 17 and a certain amount of the pretreatment material are introduced into the pretreatment unit 26 to remove one or more ion species. In step 32, the solutions 17 are then delivered into the precipitation unit 11. A certain amount of the miscible organic solvent from the organic solvent source 15 are also introduced into the precipitation device 16 to mix with the solution 17, so that one or more salt species precipitate from the solutions 17 due to their lower solubility in the miscible organic solvent and form the mixture of the precipitate solids 18 and the liquid 19.
[0034] In step 33, the precipitate solids 18 and a portion of the liquid 19 is introduced into the solid-liquid separation unit 12 for separation. In step 34, after the separation of the precipitate solids 18 from the portion of the liquid 19, the liquid 19 from the precipitation unit 11 and the solid-liquid separation unit 12 is introduced into the recovery unit 13. In non-limiting examples, the liquid 19 may be heated to a higher temperature, so that the miscible organic solvent 21 is separated from the liquid 19 within the recovery unit 13 in the form of layers of the organic phase liquid 21 and the aqueous phase liquid 20.
[0035] Subsequently, in step 35, the aqueous phase liquid 20 is introduced into the purification unit 14 for separation of the residual miscible organic solvent 22 from the aqueous phase liquid 20. In one non-limiting example, a certain amount of the pH adjustment material may be mixed with and adjust the pH values of the aqueous phase liquid 20 from the recovery unit 13 so as to ionize the residual miscible organic solvent 22, so that the residual miscible organic solvent 22 is separated and recovered after passing through the purification unit 14. In non-limiting examples, the adjusted pH values of the aqueous phase liquid 20 may be about 4-5.
[0036] In some applications, the separated miscible organic solvent 21 in step
34 and/or the recovered residual miscible organic solvents 22 in step 35 may be reintroduced into the precipitation device 16. In other applications, one or more heat exchanging steps may be employed before the precipitation step 32, the solid-liquid separation step 33, the liquid-liquid separation step 34 and/or the recovery step 35.
[0037] In non-limiting examples, prior to the precipitation step 32, the solutions 17 may be cooled, for example, to about 0°C for the subsequent precipitation step 32. The liquid-liquid separation step 34 may be performed at a higher temperature, such as about 70°C. Prior to the step 35, the aqueous phase liquid 20 from the recovery unit 13 may also be cooled, for example, to about 25° C for the recovery step 35. Additionally, in certain applications, the pretreatment step 31 and/or the solid-liquid separation step 33 may not be employed. [0038] Accordingly, in embodiments of the invention, due to the presence of the miscible organic solvent in the solution, the salt species may be removed with lower cost and higher efficiency. In addition, the residual miscible organic solvent may be readily removed with lower energy consumption via adjustment of the pH values of the aqueous phase liquid so as to produce the product liquid.
[0039] While the disclosure has been illustrated and described in typical embodiments, it is not intended to be limited to the details shown, since various modifications and substitutions can be made without departing in any way from the spirit of the present disclosure. As such, further modifications and equivalents of the disclosure herein disclosed may occur to persons skilled in the art using no more than routine experimentation, and all such modifications and equivalents are believed to be through the spirit and scope of the disclosure as defined by the subsequent claims.

Claims

WHAT IS CLAIMED IS:
1. A treatment system, comprising:
a precipitation unit configured to treat a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid;
a recovery unit in fluid communication with the precipitation unit and configured to facilitate separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents; and
a purification unit comprising one or more membrane devices in fluid communication with the recovery unit and configured to separate at least a portion of the one or more miscible organic solvents in the aqueous phase liquid from the aqueous phase liquid.
2. The treatment system of claim 1, wherein the solution comprise a saline solution.
3. The treatment system of claim 1, wherein the precipitation unit comprises an organic solvent source and a precipitation device in fluid communication with the organic solvent source, and wherein the organic solvent source is configured to provide the one or more miscible organic solvents into the precipitation device, and the precipitation device is configured to accommodate the one or more miscible organic solvents and the solution for the precipitation of the precipitate solids.
4. The treatment system of claim 1, wherein the one or more membrane devices comprises one or more of one or more reverse osmosis devices, one or more nanofiltration devices, and one or more membrane distillation devices.
5. The treatment system of claim 4, wherein the one or more membrane devices comprise the one or more reverse osmosis devices.
6. The treatment system of claim 1, wherein the purification unit further comprises an ionization source configured to provide one or more ionization materials to ionize at least a portion of the one or more organic solvents in the aqueous phase liquid so that at least a portion of the one or more ionized organic solvents are removed using the one or more membrane devices.
7. The treatment system of claim 6, wherein the ionization source comprises a pH adjustment source configured to provide one or more pH adjustment materials to adjust pH values of the aqueous phase liquid so as to ionize at least the portion of the one or more residual miscible organic solvents.
8. The treatment system of claim 1, further comprising a pretreatment unit disposed upstream from and in fluid communication with the precipitation unit, and configured to remove one or more ion species in the solution.
9. The treatment system of claim 1, further comprising a solid-liquid separation unit in fluid communication with the precipitation unit and the recovery unit for separation of the precipitation solids and the liquid.
10. The treatment system of claim 1, further comprising a plurality of heat- exchanging devices at least disposed between the precipitation unit and the recovery unit and between the recovery unit and the purification unit.
11. A treatment system, comprising:
a precipitation unit configured to treat an solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid;
a recovery unit in fluid communication with the precipitation unit and configured to facilitate separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents; and
a purification unit comprising an ionization source and a removal device in fluid communication with the recovery unit, wherein the ionization source is configured to provide one or more ionization materials to ionize at least a portion of the one or more organic solvents in the aqueous phase liquid, and the removal device is configured to receive the aqueous phase liquid to separate at least a portion of the one or more ionized residual miscible organic solvents from the aqueous phase liquid.
12. The treatment system of claim 11, wherein the precipitation unit comprises an organic solvent source and a precipitation device in fluid communication with the organic solvent source, and wherein the organic solvent source is configured to provide the one or more miscible organic solvents into the precipitation device, and the precipitation device is configured to accommodate the one or more miscible organic solvents and the solution for the precipitation of the precipitate solids.
13. The treatment system of claim 11, wherein the one or more miscible organic solvents comprises one or more of isopropylamine, propylamine, acetone, methanol, ethanol, acetonitrile, diisopropylamine, tetrahydrofuran, tetrahydropyrimidine, N-methyltetrahydropyrimidine and dioxane.
14. The treatment system of claim 11, wherein the removal device comprises one or more ion removal devices, and wherein the one or more ion removal devices comprises one or more of one or more reverse osmosis devices, one or more electrodialysis reversal devices, one or more ion exchange resins, one or more membrane distillation devices, and one or more supercapacitor desalination devices.
15. The treatment system of claim 14, wherein the one or more ion removal devices comprises one or more of the one or more reverse osmosis devices and the one or more membrane distillation devices.
16. The treatment system of claim 11, wherein the ionization source comprises a pH adjustment source configured to provide one or more pH adjustment materials to adjust pH values of the aqueous phase liquid so as to ionize at least the portion of the one or more organic solvents residual in the aqueous phase liquid.
17. The treatment system of claim 16, wherein one or more pH adjustment materials comprise one or more of hydrochloric acid and sulphuric acid.
18. The treatment system of claim 11, further comprising a pretreatment unit disposed upstream from and in fluid communication with the precipitation unit, and configured to precipitate one or more ion species in the solution.
19. The treatment system of claim 11, further comprising a plurality of heat-exchanging devices at least disposed between the precipitation unit and the recovery unit and between the recovery unit and the purification unit.
20. The treatment system of claim 11, wherein the solution comprises fracturing water.
21. A treatment process, comprising:
treating a solution using one or more miscible organic solvents to produce a mixture of precipitate solids and a liquid;
separating the liquid at least into an organic phase liquid and an aqueous phase liquid comprising a portion of the one or more miscible organic solvents; and
introducing the aqueous liquid into one or more of one or more membrane devices and one or more ion removal devices to separate at least a portion of the one or more miscible organic solvents in the aqueous phase liquid from the aqueous phase liquid.
22. The treatment process of claim 21, wherein the one or more miscible organic solvents comprises one or more of isopropylamine, propylamine, acetone, methanol, ethanol, acetonitrile, diisopropyl amine, tetrahydrofuran tetrahydropyrimidine, N-methyltetrahydropyrimidine and dioxane.
23. The treatment process of claim 21, further comprising introducing one or more ionization materials into the aqueous liquid to ionize at least a portion of the one or more miscible organic solvents in the aqueous liquid so that at least a portion of the one or more ionized organic solvents are removed using the one or more of one or more membrane devices and one or more ion removal devices.
24. The treatment process of claim 23, wherein the one or more ionization materials comprise one or more pH adjustment materials to adjust pH values of the aqueous phase liquid so as to ionize at least the portion of the one or more organic solvents in the aqueous phase liquid.
25. The treatment process of claim 24, wherein the one or more pH adjustment materials comprise one or more of hydrochloric acid and sulphuric acid.
26. The treatment process of claim 21, wherein one or more of one or more reverse osmosis devices, one or more electrodialysis reversal devices, one or more membrane distillation devices, one or more nanofiltration devices, one or more ion exchange resins, and one or more supercapacitor desalination devices are employed to separate at least the portion of the one or more miscible organic solvents residual in the aqueous phase liquid from the aqueous phase liquid.
27. The treatment process of claim 21, further pretreating the solution to reduce concentrations of one or more ion species in the solution before the solution is treated using the one or more miscible organic solvents.
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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2013066662A1 (en) * 2011-10-31 2013-05-10 General Electric Company System and process for treatment of solution
WO2014042809A1 (en) * 2012-09-13 2014-03-20 General Electric Company Treatment of produced water concentrate
WO2014042842A1 (en) * 2012-09-13 2014-03-20 General Electric Company Produced water treatment and solids precipitation from thermal treatment blowdown
US20140158616A1 (en) * 2012-12-07 2014-06-12 Advanced Water Recovery, Llc Systems, apparatus, and methods for separating salts from water

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10259734B1 (en) * 2011-04-26 2019-04-16 Mansour S. Bader Effective de-scaling for desalination plants and a new brine-forward multi-stage flash concept
US10259735B1 (en) * 2014-12-22 2019-04-16 Mansour S. Bader De-scaling methods for desalination plants and a new brine-forward multi-stage flash concept
CN103130362A (en) * 2011-11-23 2013-06-05 通用电气公司 Water treatment device and method
CA2794356C (en) 2012-09-13 2018-10-23 General Electric Company Treatment of produced water with seeded evaporator
MX2015007184A (en) * 2012-12-07 2016-03-07 Advanced Water Recovery Llc Dissolved air flotation, antisolvent crystallisation and membrane separation for separating buoyant materials and salts from water.
CN103285734B (en) * 2013-06-25 2015-07-15 深圳市森科妍科技有限公司 A treatment process and a system for waste organic solvents based on nano filter membranes
WO2020232438A1 (en) * 2019-05-16 2020-11-19 The Trustees Of Columbia University In The City Of New York Temperature swing solvent extraction for descaling of feedstreams

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1992022504A1 (en) * 1991-06-11 1992-12-23 Unilever Australia Limited Treatment of waste water
US5587088A (en) * 1995-08-01 1996-12-24 Bader; Mansour S. Precipitation and separation of inorganic species from aqueous solutions
US5961837A (en) * 1992-03-30 1999-10-05 Ferrara; Marcello Process for treatment of industrial waste
US6365051B1 (en) * 1999-10-12 2002-04-02 Mansour S. Bader Precipitation-membrane distillation hybrid system for the treatment of aqueous streams
US20050145568A1 (en) * 2001-02-01 2005-07-07 Robert Mc Ginnis Osmotic desalination process
US7501065B1 (en) * 2006-05-08 2009-03-10 Bader Mansour S Methods for treating agricultural drainage water and the like

Family Cites Families (36)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2710250A (en) * 1950-02-08 1955-06-07 Colgate Palmolive Co Apparatus for the continuous liquidliquid solvent extraction of inorganic salt impurities from organic salt solutions
US3088909A (en) 1961-02-09 1963-05-07 Richard R Davison Mixed solvents for saline water extraction
US3239459A (en) 1962-12-03 1966-03-08 Patterson Hydro Chemical Corp Separation of water from saline solution
US3177139A (en) 1963-12-02 1965-04-06 Exxon Research Engineering Co Desalination by solvent extraction
US3408290A (en) 1966-08-04 1968-10-29 Edward G. Scheibel Recovery of water from saline solution by solvent extraction
US3507782A (en) * 1967-09-08 1970-04-21 Gulf Oil Corp Separation of hydrocarbons from plant process waste water
US3823000A (en) 1969-12-04 1974-07-09 Mobil Oil Corp Recovery of potable water from sea and brackish water by selective solvent extraction
US4261818A (en) 1974-10-24 1981-04-14 Sweeney Maxwell P Method for making separations from aqueous solutions
US4430227A (en) 1980-08-18 1984-02-07 The Regents Of The University Of California Method of concentrating aqueous solutions
JPS58130121A (en) 1982-01-29 1983-08-03 Kawasaki Steel Corp Removing method of iron ion shifted to organic solvent by extraction
US4770780A (en) 1984-04-25 1988-09-13 Cf Systems Corporation Liquid CO2 /cosolvent extraction
US4706749A (en) 1984-11-06 1987-11-17 Petroleum Fermentations N.V. Method for improved oil recovery
US4763607A (en) 1986-07-03 1988-08-16 Kabushiki Kaisha Tominaga Jyushikogyosho Device for preventing the pet animal kept in the cage from escaping therefrom
US4863607A (en) 1987-08-03 1989-09-05 Resources Conservation Co. Method for removing amine from oil
US5047153A (en) 1989-10-31 1991-09-10 Resources Conservation Company Method for removing amine from solids
US5468394A (en) 1994-05-31 1995-11-21 Bader; Mansour S. Precipitation and separation of salts, scale salts, and norm contaminant salts from saline waters and saline solutions
US5562834A (en) 1995-02-14 1996-10-08 The Standard Oil Company Waste concentration and destruction process
US6537456B2 (en) * 1996-08-12 2003-03-25 Debasish Mukhopadhyay Method and apparatus for high efficiency reverse osmosis operation
AU2584299A (en) * 1998-02-09 1999-08-23 Robert L. Mcginnis Osmotic desalinization process
US6398965B1 (en) * 1998-03-31 2002-06-04 United States Filter Corporation Water treatment system and process
US7077201B2 (en) 1999-05-07 2006-07-18 Ge Ionics, Inc. Water treatment method for heavy oil production
EP1551771A1 (en) 2002-06-13 2005-07-13 Hydranautics Methods for reducing boron concentration in high salinity liquid
US20050098504A1 (en) 2002-12-11 2005-05-12 Davnor Water Treatment Technologies Ltd. Oil and gas well fracturing (frac) water treatment process
US8083942B2 (en) * 2004-12-06 2011-12-27 Board of Regents of the Nevada System of Higher Education, on Behalf of the Universary of Nevada, Reno Systems and methods for purification of liquids
US7431845B2 (en) 2005-06-23 2008-10-07 Nalco Company Method of clarifying oily waste water
US8105488B2 (en) * 2006-09-01 2012-01-31 Anticline Disposal, Llc Waste water treatment method
WO2008103814A1 (en) 2007-02-21 2008-08-28 Hpd, Llc Process for recovering heavy oil using multiple effect evaporation
CN101284704A (en) 2007-04-09 2008-10-15 株式会社日立制作所 A treatment method, device and system of organic compounds included in waste water, and asphaltum recovering system
IL187200A0 (en) 2007-11-06 2008-12-29 Asher Vitner Processes for the separation of solutes from solutions
US7963338B1 (en) * 2009-02-27 2011-06-21 Bader Mansour S Methods to treat produced water
US8409442B2 (en) * 2009-08-20 2013-04-02 Ng Innovations, Inc. Water separation method and apparatus
CN101654305B (en) 2009-09-18 2011-11-09 清华大学 Process for changing phenolic nitrate effluent into useful material by extracting, evaporating, crystallizing and coupling
CA2779280A1 (en) * 2009-10-20 2011-04-28 David Soane Treatment of wastewater
CA2781419A1 (en) 2009-11-25 2011-06-03 Massachusetts Institute Of Technology Water desalination using directional solvent extraction
US20110180479A1 (en) * 2010-01-27 2011-07-28 Milton Roy Company Zero liquid discharge water treatment system and method
MX353901B (en) * 2011-04-25 2018-02-02 Oasys Water Inc Osmotic separation systems and methods.

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1992022504A1 (en) * 1991-06-11 1992-12-23 Unilever Australia Limited Treatment of waste water
US5961837A (en) * 1992-03-30 1999-10-05 Ferrara; Marcello Process for treatment of industrial waste
US5587088A (en) * 1995-08-01 1996-12-24 Bader; Mansour S. Precipitation and separation of inorganic species from aqueous solutions
US6365051B1 (en) * 1999-10-12 2002-04-02 Mansour S. Bader Precipitation-membrane distillation hybrid system for the treatment of aqueous streams
US20050145568A1 (en) * 2001-02-01 2005-07-07 Robert Mc Ginnis Osmotic desalination process
US7501065B1 (en) * 2006-05-08 2009-03-10 Bader Mansour S Methods for treating agricultural drainage water and the like

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2013066662A1 (en) * 2011-10-31 2013-05-10 General Electric Company System and process for treatment of solution
WO2014042809A1 (en) * 2012-09-13 2014-03-20 General Electric Company Treatment of produced water concentrate
WO2014042842A1 (en) * 2012-09-13 2014-03-20 General Electric Company Produced water treatment and solids precipitation from thermal treatment blowdown
RU2662480C2 (en) * 2012-09-13 2018-07-26 БиЭл Текнолоджиз, Инк. Produced water treatment and solids precipitation from thermal treatment blowdown
US10132145B2 (en) 2012-09-13 2018-11-20 Bl Technologies, Inc. Produced water treatment and solids precipitation from thermal treatment blowdown
US10131561B2 (en) 2012-09-13 2018-11-20 Bl Technologies, Inc. Treatment of produced water concentrate
RU2687612C2 (en) * 2012-09-13 2019-05-15 БиЭл Текнолоджиз, Инк. Treatment of produced water concentrate
US20140158616A1 (en) * 2012-12-07 2014-06-12 Advanced Water Recovery, Llc Systems, apparatus, and methods for separating salts from water

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