WO2012170406A1 - Membrane desalination system and method - Google Patents
Membrane desalination system and method Download PDFInfo
- Publication number
- WO2012170406A1 WO2012170406A1 PCT/US2012/040888 US2012040888W WO2012170406A1 WO 2012170406 A1 WO2012170406 A1 WO 2012170406A1 US 2012040888 W US2012040888 W US 2012040888W WO 2012170406 A1 WO2012170406 A1 WO 2012170406A1
- Authority
- WO
- WIPO (PCT)
- 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.)
- Ceased
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
- C02F1/4693—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrodialysis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/08—Seawater, e.g. for desalination
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/06—Controlling or monitoring parameters in water treatment pH
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F5/00—Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
- C02F5/08—Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents
- C02F5/10—Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents using organic substances
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
- Y02A20/131—Reverse-osmosis
Definitions
- 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.
- membrane separation devices such as reverse osmosis (RO) devices are employed for processing such liquid steams, for example for water purification.
- 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.
- 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.
- a 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.
- FIG. 1 is a schematic diagram of a desalination system in accordance with one embodiment of the invention.
- 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.
- a feed stream 11 such as wastewater, seawater or brackish water.
- various salts may exist in the feed stream 11.
- 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.
- the desalination system 10 comprises a membrane separation device 12, a concentration device 13, and an adjustment unit 14.
- the term "membrane separation device” may generally indicate a device that is employed for desalination of a liquid stream via membrane separation.
- 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.
- 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.
- 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.
- the membrane separation device 12 comprises the reverse osmosis device.
- a permeate stream 15 and a concentrated stream 16 are produced.
- the feed stream 11 includes sparsely or partially soluble salts, such as calcium sulfate.
- the partially soluble salts may scale or precipitate within the membrane separation device 12.
- 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.
- 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.
- 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.
- 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.
- the one or more antiscalants may comprise one or more of polyacrylates, organo- phosphonates, and acrylamide copolymers.
- 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 precipitation of at least a portion of the sparsely soluble salts therein and produce a precipitated stream 17 after precipitation.
- the precipitated stream 17 may be reintroduced into the feed steam 11 for further processing in the membrane separation device 12.
- 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.
- the one or more antiscalants chelate with the sparsely soluble salts in the concentrated stream 16.
- 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.
- 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.
- the chelated ions of the sparsely soluble salts may be released for facilitation of production of the precipitation.
- the calcium ions are released and combined with sulfate ions accordingly after deactivation of the one or more antiscalants.
- 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.
- 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 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.
- 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.
- the first pH adjustment unit may be configured to provide one or more acidic additives.
- the one or more acid additives include one or more of hydrochloric acid and sulfuric acid.
- the pH of the concentrated stream 16 may be adjusted to be less than about 5.
- 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.
- 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.
- the precipitated stream 17 may include at least a portion of one or more adjusted antiscalants.
- 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.
- the activation unit 18 may not be employed.
- activation means the chelate between the one or more antiscalants and respective ions of the sparsely or partially soluble salts are recovered or connected.
- 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.
- the second pH adjustment unit may be configured to provide one or more basic additives.
- the one or more basic additives include one or more of sodium hydroxide, potassium hydroxide, and ammonia hydroxide.
- 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.
- FIG. 1 is merely illustrative.
- 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.
- 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.
- the feed stream 11 including the one or more antiscalants is introduced into the membrane separation device 12 for desalination.
- 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.
- 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.
- 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.
- the precipitate may occur in the concentration device 13.
- the precipitated stream 17 from the concentration device 13 is reintroduced into the membrane separation device 12 for further processing so as to improve water recovery.
- the activation unit 18 may be provided to activate at least a portion of the one or more antiscalants in the precipitated stream 17.
- the step for activation of at least a portion of the one or more antiscalants in the precipitated stream 17 may not employed.
- 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.
- the water recovery may be improved and the possibility for the scale formation within the membrane separation device 12 may also be reduced.
- 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.
- 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.
- 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.
- 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.
- the concentrated stream 16 comprises an about 200ml CaS0 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 CaS0 4 to precipitate out at the supersaturated level.
- the conductivity of the solution is about 19.23 mS/cm
- the pH is about 6.5
- turbidity is about 0.113 NTU.
- a lmol/1 hydrochloric acid (HC1) solution is added into the CaS0 4 solution to adjust the pH of the CaS0 4 solution to be about 1.3 so as to adjust the antiscalant.
- the CaS0 4 solution become turbid after the pH adjustment and CaS0 4 particles are observed in the solution.
- the conductivity of the CaS0 4 solution after adjustment is about 15.37 mS/cm
- the pH is about 1.3
- the turbidity is about 4226 NTU, which indicates the CaS0 4 precipitate are produced.
- the concentrated stream 16 comprises an about 200ml CaS0 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 CaS0 4 to precipitate out at the supersaturated level.
- the conductivity of the solution is about 19.23 mS/cm
- the pH is about 6.5
- turbidity is about 0.113 NTU.
- the solution is heated to about 100°C so as to adjust the antiscalant, and then cooled down to a room temperature.
- the CaS0 4 solution become turbid during the heating process, and the CaS0 4 particles are observed in the solution.
- the conductivity of the CaS0 4 solution after adjustment is about 15.61 mS/cm
- the pH was 1.7
- the turbidity is about 3175 NTU, which also indicates the CaS0 4 precipitate are produced.
- the adjustment unit 14 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.
- the concentration of the sparsely soluble salts in the precipitated stream 17 may be reduced.
- 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.
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- 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
Description
Claims
Priority Applications (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| RU2013153467/05A RU2013153467A (en) | 2011-06-10 | 2012-06-05 | INSTALLATION AND METHOD OF MEMBRANE DESALIZATION |
| CA2837210A CA2837210A1 (en) | 2011-06-10 | 2012-06-05 | Membrane desalination system and method |
| AU2012268364A AU2012268364A1 (en) | 2011-06-10 | 2012-06-05 | Membrane desalination system and method |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201110155282.9A CN102815810B (en) | 2011-06-10 | 2011-06-10 | Desalination system and desalination method |
| CN201110155282.9 | 2011-06-10 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2012170406A1 true WO2012170406A1 (en) | 2012-12-13 |
Family
ID=46246281
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/US2012/040888 Ceased WO2012170406A1 (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) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US10589188B2 (en) | 2016-06-27 | 2020-03-17 | Enviro Water Minerals Company, Inc. | System and method for removal of scale forming components |
Families Citing this family (3)
| 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 |
| 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 |
Citations (5)
| 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 |
| US6036867A (en) * | 1995-12-13 | 2000-03-14 | Degremont | Method for desalinating and demineralizing solutions containing acids and/or metal salts |
| WO2008108636A1 (en) * | 2007-03-05 | 2008-09-12 | Stichting Wetsus Centre Of Excellence For Sustainable Water Technology | Method and system for purifying a liquid comprising crystal inhibitor recovery |
| WO2009152148A1 (en) * | 2008-06-11 | 2009-12-17 | The Regents Of The University Of California | Method and system for high recovery water desalting |
| WO2010033674A1 (en) * | 2008-09-17 | 2010-03-25 | Siemens Water Technologies Corp. | High recovery sulfate removal process |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CA2186963C (en) * | 1996-10-01 | 1999-03-30 | Riad A. Al-Samadi | High water recovery membrane purification 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 |
-
2011
- 2011-06-10 CN CN201110155282.9A patent/CN102815810B/en active Active
-
2012
- 2012-06-05 CA CA2837210A patent/CA2837210A1/en not_active Abandoned
- 2012-06-05 AU AU2012268364A patent/AU2012268364A1/en not_active Abandoned
- 2012-06-05 WO PCT/US2012/040888 patent/WO2012170406A1/en not_active Ceased
- 2012-06-05 RU RU2013153467/05A patent/RU2013153467A/en not_active Application Discontinuation
Patent Citations (5)
| 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 |
| US6036867A (en) * | 1995-12-13 | 2000-03-14 | Degremont | Method for desalinating and demineralizing solutions containing acids and/or metal salts |
| WO2008108636A1 (en) * | 2007-03-05 | 2008-09-12 | Stichting Wetsus Centre Of Excellence For Sustainable Water Technology | Method and system for purifying a liquid comprising crystal inhibitor recovery |
| WO2009152148A1 (en) * | 2008-06-11 | 2009-12-17 | The Regents Of The University Of California | Method and system for high recovery water desalting |
| WO2010033674A1 (en) * | 2008-09-17 | 2010-03-25 | Siemens Water Technologies Corp. | High recovery sulfate removal process |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US10589188B2 (en) | 2016-06-27 | 2020-03-17 | Enviro Water Minerals Company, Inc. | System and method for removal of scale forming components |
| US11351475B2 (en) | 2016-06-27 | 2022-06-07 | Enviro Water Minerals Company, Inc. | System and method for removal of scale forming components |
Also Published As
| Publication number | Publication date |
|---|---|
| RU2013153467A (en) | 2015-07-20 |
| CA2837210A1 (en) | 2012-12-13 |
| CN102815810A (en) | 2012-12-12 |
| AU2012268364A1 (en) | 2014-01-09 |
| CN102815810B (en) | 2015-04-22 |
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