AU2012268364A1 - Membrane desalination system and method - Google Patents

Membrane desalination system and method Download PDF

Info

Publication number
AU2012268364A1
AU2012268364A1 AU2012268364A AU2012268364A AU2012268364A1 AU 2012268364 A1 AU2012268364 A1 AU 2012268364A1 AU 2012268364 A AU2012268364 A AU 2012268364A AU 2012268364 A AU2012268364 A AU 2012268364A AU 2012268364 A1 AU2012268364 A1 AU 2012268364A1
Authority
AU
Australia
Prior art keywords
stream
membrane separation
adjustment unit
antiscalants
separation device
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
AU2012268364A
Inventor
Wei Cai
Zijun Xia
Rihua Xiong
Chengqian Zhang
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.)
General Electric Co
Original Assignee
General Electric Co
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 General Electric Co filed Critical General Electric Co
Publication of AU2012268364A1 publication Critical patent/AU2012268364A1/en
Abandoned legal-status Critical Current

Links

Classifications

    • 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
    • C02F1/02Treatment 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
    • C02F1/46Treatment 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
    • C02F1/4693Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrodialysis
    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F2001/007Processes including a sedimentation step
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F5/00Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
    • C02F5/08Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents
    • C02F5/10Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents using organic substances
    • 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
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

[0042] A desalination system comprises a membrane separation device (12) and an adjustment unit (14). The membrane separation device (12) is configured to receive a feed stream (11) including one or more antiscalants and produce a permeate stream (15) and a concentrated stream (16). The adjustment unit (14) is configured to adjust at least a portion of the one or more antiscalants in the concentrated stream (16) from the membrane separation device (12)by decreasing pH of the concentrated stream or by increasing the temperature of the concentrated stream, thereby releasing ions of sparsely soluble salts from their complexes with the antiscalants. The precipitated is separated in a concentration device (13). The concentrated stream is returned to the feed side of the membrane separation device (12), the pH being increased in stream (17) by means of an activation device (18). A desalination method is also presented.

Description

WO 2012/170406 PCT/US2012/040888 MEMBRANE DESALINATION SYSTEM AND METHOD BACKGROUND OF THE DISCLOSURE [0001] The invention relates generally to desalination systems and methods for water recovery. More particularly, this invention relates to desalination systems and methods employing membrane separation devices for water recovery. [0002] In industrial processes, large amounts of wastewater, such as aqueous saline solutions are produced. Generally, such wastewater is not suitable for direct consumption in domestic or industrial applications. In view of the limited eligible water sources, it is desirable to recover eligible water from liquid streams, such as wastewater, seawater or brackish water. [0003] Typically, membrane separation devices, such as reverse osmosis (RO) devices are employed for processing such liquid steams, for example for water purification. Generally, such liquid streams may include sparsely soluble salts, such as calcium sulfates. Due to solubility limits of such sparsely soluble salts in the liquid streams, during processing, the sparsely soluble salts may scale or precipitate on membranes of the membrane separation devices, which results in loss of permeate flux through the membranes and damage to the membrane separation devices. [0004] There have been attempts to inhibit scale formation of the sparsely soluble salts within the membrane separation devices during processing of the liquid streams. For example, antiscalants have been widely used to inhibit the scale formation of the sparsely soluble salts so as to increase efficiency of water recovery. However, due to limits of concentration tolerance of the sparsely soluble salts in the liquid streams, although the antiscalants are used, in current applications, the sparsely soluble salts may still scale or precipitate to damage the membranes, which is disadvantageous for the membrane separation devices for water recovery. [00051 Therefore, there is a need for new and improved desalination systems and methods employing membrane separation devices to avoid the scale formation of 1 WO 2012/170406 PCT/US2012/040888 the sparsely soluble salts and increase the water recovery during processing of liquid streams. BRIEF DESCRIPTION OF THE DISCLOSURE [0006] A desalination system is provided in accordance with one embodiment of the invention. The desalination system comprises a membrane separation device and an adjustment unit. The membrane separation device is configured to receive a feed stream including one or more antiscalants and produce a permeate stream and a concentrated stream. The adjustment unit is configured to adjust at least a portion of the one or more antiscalants in the concentrated stream from the membrane separation device. [0007] A desalination method is provided in accordance with another embodiment of the invention. The desalination method comprises passing a first stream including one or more antiscalants through a membrane separation device to produce a permeate stream and a concentrated stream, and adjusting at least a portion of the one or more antiscalants in the concentrated stream from the membrane separation device. [0008] These and other advantages and features will be better understood from the following detailed description of preferred embodiments of the invention that is provided in connection with the accompanying drawings. BRIEF DESCRIPTION OF THE DRAWINGS [0009] FIG. 1 is a schematic diagram of a desalination system in accordance with one embodiment of the invention. DETAILED DESCRIPTION OF THE INVENTION [0010] Preferred embodiments of the present disclosure will be described hereinbelow with reference to the accompanying drawings. In the following 2 WO 2012/170406 PCT/US2012/040888 description, well-known functions or constructions are not described in detail to avoid obscuring the disclosure in unnecessary detail. [0011] FIG. 1 illustrates a schematic diagram of a desalination system 10 in accordance with on embodiment of the invention for processing, for example, for purification of a feed stream 11, such as wastewater, seawater or brackish water. In some examples, various salts may exist in the feed stream 11. In some examples, the salts may include soluble salts and sparsely or partially soluble salts. Non-limiting examples of the soluble salts include sodium chloride and magnesium chloride. Non limiting examples of the sparsely or partially soluble salts include calcium sulfate and barium sulfate. In one example, the sparsely or partially soluble salts include calcium sulfate. [0012] As illustrated in FIG. 1, the desalination system 10 comprises a membrane separation device 12, a concentration device 13, and an adjustment unit 14. For some arrangements, the term "membrane separation device" may generally indicate a device that is employed for desalination of a liquid stream via membrane separation. During the membrane separation, with introduction of a liquid stream into the membrane separation device, at least a portion of the liquid stream may permeate or pass through a membrane (not shown) of the membrane separation device as a result of a driving force(s) to produce a permeate stream. Meanwhile, another portion of the liquid stream may not permeate or pass through the membrane and may be retained by the membrane to produce a concentrated stream. In some applications, the permeate stream may be a dilute stream having a lower concentration of the salts than the liquid stream. The concentrated stream may have a higher concentration of the salts than the liquid stream. [0013] In embodiments of the invention, the membrane separation device 12 may not comprise any specific membrane separation devices. Non-limiting examples of the membrane separation device 12 may comprise a reverse osmosis device, a nanofiltration device, an electrodialysis device, an electrodialysis reversal device, a membrane distillation device, or combinations thereof. In one example, the membrane separation device 12 comprises the reverse osmosis device. 3 WO 2012/170406 PCT/US2012/040888 [00141 In the illustrated example in FIG. 1, the membrane separation device 12 is configured to process, for example, for purification of the feed stream 11. With the introduction of the feed stream 11 into the membrane separation device 12, a permeate stream 15 and a concentrated stream 16 are produced. [00151 In some applications, the feed stream 11 includes sparsely or partially soluble salts, such as calcium sulfate. During desalination of the feed stream 11, with the increase of the concentration of the partially soluble salts, the partially soluble salts may scale or precipitate within the membrane separation device 12. [0016] For some arrangements, in order to avoid or inhibit the scale formation, one or more antiscalants may be added into the feed stream 11 before the feed stream 11 is introduced into the membrane separation device 12, so that the one or more antiscalants may chelate with ions of the sparsely soluble salts to inhibit the scale formation within the membrane separation device 12. For example, the one or more antiscalants chelate with calcium ions of the calcium sulfate, and thus the sulfate ions may not combined with calcium ions so as to inhibit the scale formation of the calcium sulfate. [00171 Accordingly, during the desalination, the concentrated stream 16 is produced and at least includes a portion of the components in the feed stream 11, such as the one or more antiscalants, the sparsely soluble salts, and other salts including, but not limited to the soluble salts, which are separated by the membrane of the membrane separation device 12. [00181 In some examples, the one or more antiscalants may not comprise any specific antiscalants and may be selected based on different applications, for example base on species of the sparsely or partially soluble salts. In non-limiting examples, the one or more antiscalants may comprise one or more of polyacrylates, organo phosphonates, and acrylamide copolymers. [0019] For the illustrated arrangement, the concentration device 13 is in fluid communication with the membrane separation device 12 and configured to receive the concentrated stream 16 from the membrane separation device 12 so as to facilitate 4 WO 2012/170406 PCT/US2012/040888 precipitation of at least a portion of the sparsely soluble salts therein and produce a precipitated stream 17 after precipitation. In certain applications, in order to improve water recovery of the feed stream 11, the precipitated stream 17 may be reintroduced into the feed steam 11 for further processing in the membrane separation device 12. In non-limiting examples, the concentration device 13 may comprise a container for accommodation of the concentrated stream 16. The precipitate and a portion of a stream may be discharged from a bottom portion (not labeled) of the concentration device 13 through a pipeline 19. [0020] For some arrangements, the one or more antiscalants chelate with the sparsely soluble salts in the concentrated stream 16. For facilitating the precipitation of the sparsely soluble slats in the concentration device 13, as depicted in FIG. 1, the adjustment unit 14 is employed to be in fluid communication with the concentration device 13 for adjustment, for example, for deactivation of at least a portion of the one or more antiscalants so that the chelate between the one or more antiscalants and the sparsely soluble salts is changed, for example, deactivated accordingly. [0021] In some applications, the term "adjustment of at least a portion of the one or more antiscalants" means the chelate between the at least a portion of the one or more antiscalants and respective ions of the sparsely or partially soluble salts is adjusted, for example, deactivated or disconnected so that the chelated ions of the sparsely soluble salts are released for formation of the precipitation. [0022] Thus, the chelated ions of the sparsely soluble salts may be released for facilitation of production of the precipitation. For example, the calcium ions are released and combined with sulfate ions accordingly after deactivation of the one or more antiscalants. When the concentration of the sparsely or partially soluble salts in the concentrated stream 16 is in a relative higher level, such as in a saturation level or a supersaturation level, the precipitation of the sparsely soluble salts may occur. [0023] In some applications, the precipitation of the sparsely or partially soluble salts may not occur until the degree of the saturation or supersaturation thereof is very high. Accordingly, in certain examples, seed particles (not shown) may be added into the concentration device 13 to induce the precipitation at a relative 5 WO 2012/170406 PCT/US2012/040888 lower concentration of the sparsely soluble salts. In certain applications, the seed particles may comprise solid particles including, but not limited to calcium sulfate particles and their hydrates to induce the precipitation. [0024] In some embodiments, the adjustment unit 14 may comprise a first pH adjustment unit configured to decrease pH of the concentrated stream 16 for adjustment of at least a portion of the one or more antiscalants. In non-limiting examples, the first pH adjustment unit may be configured to provide one or more acidic additives. Non-limiting examples of the one or more acid additives include one or more of hydrochloric acid and sulfuric acid. In certain examples, the pH of the concentrated stream 16 may be adjusted to be less than about 5. [00251 For the illustrated arrangement, the adjustment unit 14 adjusts at least a portion of the one or more antiscalants in the concentrated stream 16 after the concentrated stream 16 is introduced into the concentration device 13. Alternatively, the adjustment unit 14 may adjust at least a portion of the one or more antiscalants prior to the introduction of the concentrated stream 16 into the concentration device 13. [0026] In some examples, the precipitated stream 17 may include at least a portion of one or more adjusted antiscalants. Before the precipitated stream 17 is mixed into the feed stream 11, the desalination system 10 may further comprise an activation unit 18 in fluid communication with the concentration device 13 and configured to activate at least a portion of the one or more adjusted antiscalants therein, so that at least a portion of the one or more antiscalants in the precipitated stream 17 may be reused after introduction of the precipitated stream 17 into the feed stream 11 for chelate with respective ions of the sparsely or partially soluble salts. In other examples, the activation unit 18 may not be employed. As used herein, the term "activation" means the chelate between the one or more antiscalants and respective ions of the sparsely or partially soluble salts are recovered or connected. [00271 For some arrangements, the activation unit 18 may comprise a second pH adjustment unit configured to increase the pH of the precipitated stream 17 from the concentration device 13. In non-limiting examples, the second pH adjustment unit 6 WO 2012/170406 PCT/US2012/040888 may be configured to provide one or more basic additives. Non-limiting examples of the one or more basic additives include one or more of sodium hydroxide, potassium hydroxide, and ammonia hydroxide. In certain examples, the pH of the precipitated stream 17 may be adjusted to be greater than the pH of the concentrated stream 16. The pH of the activation unit 18 may be greater than the pH of the adjustment unit 14. Based on different species of the one or more antiscalants, the pH of the concentrated and precipitated streams 16, 17 may vary after adjustment. [0028] It should be noted that the arrangement in FIG. 1 is merely illustrative. In the illustrated example, one membrane separation device 12 is illustrated and the activation unit 18 is configured to activate the antiscalants before the precipitated stream 17 is mixed into the feed stream 11. In other applications, more than one membrane separation device may be employed. The activation unit 18 may activate at least a portion of the one or more antiscalants in the precipitate stream 17 after the precipitate stream 17 is mixed into the feed stream 11. [0029] Accordingly, during operation, the feed stream 11 including the one or more antiscalants is introduced into the membrane separation device 12 for desalination. With the introduction of the feed stream 11, the permeate stream 15 and the concentrated stream 16 are produced. Due to the chelate between the one or more antiscalants and at least a portion of the sparsely soluble salts, the scale formation may be avoid or inhibited so as to ensure operation of the membrane separation device 12. [0030] Subsequently, the concentrated stream 16 at least including a portion of the one or more antiscalants and a portion of the sparsely soluble salts are introduced into the concentration device 13. Meanwhile, the adjustment unit 14 provides the one or more acid additives to adjust at least a portion of the one or more antiscalants so as to release the ions chelated with the one or more antiscalants. With the increase of the concentration of the sparsely soluble salts in the concentrated stream 16, the precipitate may occur in the concentration device 13. [00311 Finally, the precipitated stream 17 from the concentration device 13 is reintroduced into the membrane separation device 12 for further processing so as to 7 WO 2012/170406 PCT/US2012/040888 improve water recovery. In some examples, prior to introduction of the precipitated stream 17 into the membrane separation device 12, the activation unit 18 may be provided to activate at least a portion of the one or more antiscalants in the precipitated stream 17. Alternatively, the step for activation of at least a portion of the one or more antiscalants in the precipitated stream 17 may not employed. [0032] Thus, for some arrangements, due to existence of the one or more antiscalants in the feed stream 11, during operation, the scale formation may be inhibited. In addition, the adjustment unit 14 may be employed to adjust at least a portion of the one or more antiscalants in the concentrated stream 16 so as to facilitate the precipitation in the concentration device 13 and reduce the concentration of the sparsely or partially soluble salts in the precipitated stream 17. After the precipitated stream 17 is reintroduced into the membrane separation device 12, the water recovery may be improved and the possibility for the scale formation within the membrane separation device 12 may also be reduced. [0033] As illustrated in FIG. 1, in certain applications, the adjustment unit 14 may comprise a temperature adjustment unit for adjustment of at least a portion of the one or more antiscalants in the concentrated stream 16. In some examples, the temperature adjustment unit may be configured to increase the temperature of the concentrated stream 16. Non-limiting examples of the temperature adjustment unit include a heater. [0034] Similarly, during operation, prior to or after the concentrated stream 16 from the membrane separation device 12 is introduced into the concentration device 13, the temperature adjustment unit heats the concentrated stream 16 to adjust at least a portion of the one or more antiscalants for facilitation of the precipitate. In other applications, the seed particles may also be employed in the concentration device 13. The activation unit 18 may or may not be employed when the temperature adjustment unit 14 is employed. [00351 Two non-limiting examples are now described to illustrate the operations of the adjustment unit 14 comprising the first pH adjustment unit and the temperature adjustment unit of the desalination system 10. For easy illustration, the 8 WO 2012/170406 PCT/US2012/040888 sparsely soluble salts of the calcium sulfate (CaSO 4 ) in the concentrated stream 16 are taken as an example. EXAMPLE 1 [00361 In this exemplary experiment, the concentrated stream 16 comprises an about 200ml CaSO 4 solution with 600% supersaturation level. An antiscalant (MDC 151 from GE Water & Process Technologies) of about 3ppm exist in the solution to inhibit the CaSO 4 to precipitate out at the supersaturated level. Under this condition, the conductivity of the solution is about 19.23 mS/cm, the pH is about 6.5 and turbidity is about 0.113 NTU. [00371 Subsequently, a 1mol/l hydrochloric acid (HCl) solution is added into the CaSO 4 solution to adjust the pH of the CaSO 4 solution to be about 1.3 so as to adjust the antiscalant. Under such a condition, the CaSO 4 solution become turbid after the pH adjustment and CaSO 4 particles are observed in the solution. After the pH adjustment, the conductivity of the CaSO 4 solution after adjustment is about 15.37 mS/cm, the pH is about 1.3 and the turbidity is about 4226 NTU, which indicates the CaSO 4 precipitate are produced. EXAMPLE 2 [00381 In this exemplary experiment, the concentrated stream 16 comprises an about 200ml CaSO 4 solution with 600% supersaturation level. An antiscalant (MDC 151 from GE Water & Process Technologies) of about 3ppm exist in the solution to inhibit the CaSO 4 to precipitate out at the supersaturated level. Under this condition, the conductivity of the solution is about 19.23 mS/cm, the pH is about 6.5 and turbidity is about 0.113 NTU. [00391 Subsequently, the solution is heated to about 100 C so as to adjust the antiscalant, and then cooled down to a room temperature. The CaSO 4 solution become turbid during the heating process, and the CaSO 4 particles are observed in the solution. After being cooled down to the room temperature, under such a condition, the conductivity of the CaSO 4 solution after adjustment is about 15.61 mS/cm, the pH 9 WO 2012/170406 PCT/US2012/040888 was 1.7 and the turbidity is about 3175 NTU, which also indicates the CaSO 4 precipitate are produced. [0040] From the above two exemplary experiments, due to the employment of the adjustment unit 14, at least a portion of the one or more antiscalants in the concentrated stream 16 may be adjusted to facilitate the precipitate of the sparsely soluble salts. Thus, the concentration of the sparsely soluble salts in the precipitated stream 17 may be reduced. As a result, when the precipitated stream 17 is reintroduced into the membrane separation device 12, the water recovery may be improved and the possibility for the scale formation within the membrane separation device 12 may also be alleviated. For some arrangements, the activation unit 18 may also be employed to activate at least a portion of the one or more antiscalants in the precipitated stream 17 for recycle of at least a portion of the one or more antiscalants. [0041] 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 within the spirit and scope of the disclosure as defined by the following claims. 10

Claims (20)

1. A desalination system, comprising: a membrane separation device configured to receive a feed stream including one or more antiscalants and produce a permeate stream and a concentrated stream; and an adjustment unit configured to adjust at least a portion of the one or more antiscalants in the concentrated stream from the membrane separation device.
2. The desalination system of claim 1, wherein the feed stream comprises sparsely soluble salts, and wherein the adjustment unit is configured to disconnect chelate between the one or more antiscalants and ions of the sparsely soluble salts.
3. The desalination system of claim 1, wherein the adjustment unit comprises one or more of a first pH adjustment unit and a temperature adjustment unit.
4. The desalination system of claim 3, wherein the first pH adjustment unit is in fluid communication with the membrane separation device and configured to decrease pH of the concentrated stream from the membrane separation device.
5. The desalination system of claim 4, further comprising a concentration device in fluid communication with the membrane separation device and configured to receive the concentrated stream from the membrane separation device.
6. The desalination system of claim 5, further comprising an activation unit in fluid communication with the concentration device and configured to activate at least a portion of the one or more antiscalants in a precipitated stream from the concentration device.
7. The desalination system of claim 6, wherein the activation unit comprises a second pH adjustment unit configured to increase pH of the precipitated stream.
8. The desalination system of claim 7, wherein the pH of the activation unit is higher than the pH of the adjustment unit. 11 WO 2012/170406 PCT/US2012/040888
9. The desalination system of claim 1, further comprising seed particles disposed in the concentration device for facilitation precipitation.
10. The desalination system of claim 1, wherein the membrane device comprises one or more of a reverse osmosis device, a nanofiltration device, a microfiltration device, an ultrafiltration device, and a membrane distillation device.
11. A desalination method, comprising: passing a first stream including one or more antiscalants through a membrane separation device to produce a permeate stream and a concentrated stream; and adjusting at least a portion of the one or more antiscalants in the concentrated stream from the membrane separation device.
12. The desalination method of claim 11, wherein the adjusting step is performed via an adjustment unit, and wherein the adjustment unit comprises one or more of a first pH adjustment unit and a temperature adjustment unit.
13. The desalination method of claim 12, wherein the adjusting step comprising heating the concentrated stream through the temperature adjustment unit.
14. The desalination method of claim 12, wherein the first pH adjustment unit is in fluid communication with the membrane separation device and configured to decrease pH of the concentrated stream from the membrane separation device.
15 The desalination method of claim 14, further comprising introducing the concentrated stream from the membrane separation device into a concentration device and produce a precipitated stream.
16 The desalination method of claim 15, further comprising introducing seed particles into the concentration device to facilitate precipitation.
17. The desalination method of claim 15, further comprising activating at least a portion of the one or more antiscalants in the precipitated stream via an activation unit. 12 WO 2012/170406 PCT/US2012/040888
18. The desalination method of claim 17, wherein the activation unit comprises a second pH adjustment unit configured to increase pH of the precipitated stream.
19. The desalination method of claim 18, wherein the pH of the precipitated stream is higher than the pH of the concentrated stream after pH adjustment.
20. The desalination method of claim 11, wherein the feed stream comprises partially soluble salts, and wherein chelate between the one or more antiscalants and ions of the partially soluble salts is disconnected in the adjusting step. 13
AU2012268364A 2011-06-10 2012-06-05 Membrane desalination system and method Abandoned AU2012268364A1 (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
CN201110155282.9 2011-06-10
CN201110155282.9A CN102815810B (en) 2011-06-10 2011-06-10 Desalination system and desalination method
PCT/US2012/040888 WO2012170406A1 (en) 2011-06-10 2012-06-05 Membrane desalination system and method

Publications (1)

Publication Number Publication Date
AU2012268364A1 true AU2012268364A1 (en) 2014-01-09

Family

ID=46246281

Family Applications (1)

Application Number Title Priority Date Filing Date
AU2012268364A Abandoned AU2012268364A1 (en) 2011-06-10 2012-06-05 Membrane desalination system and method

Country Status (5)

Country Link
CN (1) CN102815810B (en)
AU (1) AU2012268364A1 (en)
CA (1) CA2837210A1 (en)
RU (1) RU2013153467A (en)
WO (1) WO2012170406A1 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107445328A (en) * 2016-05-31 2017-12-08 通用电气公司 The processing method and system of salt solution
CN106115740B (en) * 2016-06-13 2017-06-30 神华集团有限责任公司 A kind of salt extraction process and salt making system
US10589188B2 (en) 2016-06-27 2020-03-17 Enviro Water Minerals Company, Inc. System and method for removal of scale forming components
CN109205898B (en) * 2017-07-05 2022-06-17 国家能源投资集团有限责任公司 Treatment method and treatment system for brackish water or seawater

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5501798A (en) * 1994-04-06 1996-03-26 Zenon Environmental, Inc. Microfiltration enhanced reverse osmosis for water treatment
FR2742430B1 (en) * 1995-12-13 1998-09-04 Degremont DESALINATION AND DEMINERALIZATION OF SOLUTIONS CONTAINING ACIDS AND / OR METAL SALTS
CA2186963C (en) * 1996-10-01 1999-03-30 Riad A. Al-Samadi High water recovery membrane purification process
NL2000640C2 (en) * 2007-03-05 2008-09-08 Stichting Wetsus Ct Of Excelle Method and system for purifying a liquid.
US20110155665A1 (en) * 2008-06-11 2011-06-30 The Regents Of The University Of California Method and System for High Recovery Water Desalting
US20110163032A1 (en) * 2008-09-17 2011-07-07 Siemens Pte Ltd High recovery sulfate removal process
CN201801433U (en) * 2010-08-06 2011-04-20 华润怡宝食品饮料(深圳)有限公司 Concentrated water recovering system

Also Published As

Publication number Publication date
WO2012170406A1 (en) 2012-12-13
CN102815810A (en) 2012-12-12
CA2837210A1 (en) 2012-12-13
RU2013153467A (en) 2015-07-20
CN102815810B (en) 2015-04-22

Similar Documents

Publication Publication Date Title
CA2812225C (en) Membrane filtration process with retentate recovery and carbon dioxide injection
US10226740B2 (en) Membrane and electrodialysis based seawater desalination with salt, boron and gypsum recovery
US20110155665A1 (en) Method and System for High Recovery Water Desalting
US20090039020A1 (en) Methods for reducing boron concentration in high salinity liquid
US10370275B2 (en) System for removing minerals from a brine
CN104692574A (en) Treatment method of high saline wastewater
AU2014215005A1 (en) Osmotic separation systems and methods
JP6189205B2 (en) Concentrator scale detection device and method, water regeneration treatment system
JPH10503414A (en) Reverse osmosis for water treatment enhanced by microfiltration
JP2015029932A (en) Desalinator and desalinating method as well as method for simultaneously producing freshwater, salt, and valuable matters
EP2547628A1 (en) Systems and processes for treatment of solutions
AU2012268364A1 (en) Membrane desalination system and method
CN108623055B (en) Zero-discharge softening process and device for pulping and papermaking wastewater
KR102042043B1 (en) A Draw Solution for forward osmosis using salt of organic acid and use thereof
CN105198141A (en) High-temperature high-salinity wastewater zero-discharging method
JP6231806B2 (en) Desalination apparatus and desalination method, and method of co-production of fresh water, salt and valuables
JP2018502710A (en) Method and system for solar driven osmotic water purification
JP7212490B2 (en) Water treatment device and water treatment method
WO2013066662A1 (en) System and process for treatment of solution
JP6266257B2 (en) Desalination apparatus and desalination method
JP7228492B2 (en) Water treatment device and water treatment method
JP6524752B2 (en) Method of treating calcium ion and inorganic carbon containing water
KR101501656B1 (en) The method for utilizing concentrated-water produced from desalination by reverse osmosis
CN111051253A (en) Apparatus and method for treating silica-containing water
JP2006167533A (en) Method for condensing sea water

Legal Events

Date Code Title Description
MK5 Application lapsed section 142(2)(e) - patent request and compl. specification not accepted