KR20100134553A - Method of purifying water containing metallic ingredient and apparatus for purification - Google Patents
Method of purifying water containing metallic ingredient and apparatus for purification Download PDFInfo
- Publication number
- KR20100134553A KR20100134553A KR1020107016452A KR20107016452A KR20100134553A KR 20100134553 A KR20100134553 A KR 20100134553A KR 1020107016452 A KR1020107016452 A KR 1020107016452A KR 20107016452 A KR20107016452 A KR 20107016452A KR 20100134553 A KR20100134553 A KR 20100134553A
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- KR
- South Korea
- Prior art keywords
- water
- metal component
- reverse osmosis
- osmosis membrane
- alkaline
- Prior art date
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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
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/58—Multistep processes
-
- 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
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/4618—Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water
-
- 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
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/463—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrocoagulation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/025—Reverse osmosis; Hyperfiltration
-
- 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
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/4618—Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water
- C02F2001/4619—Devices therefor; Their operating or servicing for producing "ionised" acidic or basic water only cathodic or alkaline water, e.g. for reducing
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
Abstract
An object of the present invention is to provide a method for purifying a metal component-containing water capable of reducing the processing burden of concentrated water produced by reverse osmosis membrane separation.
The present invention is a method for purifying a metal component-containing water, which performs a reverse osmosis membrane separation step of separating the metal component-containing water in which the metal component is dissolved into purified water and concentrated water, which is permeate water, by reverse osmosis membrane separation. And an electrolytic step of electrolyzing the concentrated water to obtain alkaline water at the cathode side, and a precipitate separation step of filtering and separating the metal component precipitated by being alkaline from the alkaline water obtained in the electrolytic step. Provided is a method for purifying a component-containing water.
Description
The present invention purifies a metal component-containing water which obtains purified water by reverse osmosis membrane separation of metal component-containing water, such as sewage, factory drainage, groundwater, river water, landfill leachate, and seawater in which a metal component is dissolved. A method and a purification treatment apparatus.
Conventionally, as this kind of purification treatment method, a depositing step of depositing a metal component-containing water in which a metal component is dissolved with a depositing device such as a MF membrane filtration device, and a depositing process deposited by the depositing step A method of performing a reverse osmosis membrane separation step of separating water into permeate and concentrated water by reverse osmosis membrane separation is known.
In such a method, the permeated water by separation of the reverse osmosis membrane becomes purified water, and since the concentrated water contains many metal components, it cannot be disposed of as it is, but by solidifying and embedding the metal components by separate evaporation concentration treatment, etc. Is being processed.
However, the conventional purification treatment method has a problem that a huge burden is required for the treatment of the concentrated water, such as a large amount of energy is required to evaporate water in the treatment of the concentrated water produced by the reverse osmosis membrane separation. have.
In view of the above conventional problems, the present invention has an object to provide a method for purifying a metal component-containing water and a purifying treatment apparatus capable of at least reducing the processing burden of the concentrated water produced by the reverse osmosis membrane separation. .
MEANS TO SOLVE THE PROBLEM In order to solve the said subject, this invention provides the metal component containing water which performs the reverse osmosis membrane separation process which isolate | separates the metal component containing water which the metal component melt | dissolves into the purified water and concentrated water which are permeate water by reverse osmosis membrane separation. As a purification treatment method, further, an electrolytic step of electrolyzing the concentrated water to obtain alkaline water at the cathode side, and a precipitate separation step of filtration-separating the metal component precipitated by being alkaline from the alkaline water obtained in the electrolytic step. Provided is a method for purifying a metal component-containing water, characterized by the above-mentioned.
In the method for purifying the metal component-containing water, alkaline water in which the metal component is concentrated on the cathode side can be obtained by electrolysis in the electrolytic step, and the metal component precipitated by becoming alkaline by the precipitate separation step. Can be separated by filtration. Therefore, the processing burden of evaporation concentration for depositing and solidifying a metal component can be significantly reduced. In addition, the metal component isolate | separated by filtration can be removed, for example by backwashing. At this time, the generated backwash waste liquid may contain a metal component at a much higher concentration than the concentrated water separated by the reverse osmosis membrane. Therefore, even when backwashing, the processing burden of evaporation concentration can be remarkably reduced.
In the present invention, a depositing step of depositing the metal component-containing water before the reverse osmosis membrane separation step in a depositing apparatus is performed, and in the reverse osmosis membrane separation step, the reverse osmosis of the metal component-containing water deposited in the depositing step is performed. It is preferable to isolate | separate a membrane and to separate the precipitated metal component in the said depositing apparatus in the said precipitate separation process.
In such a method, the burden on the reverse osmosis membrane can be reduced by depositing in advance in the depositing step. In addition, in the precipitate separation step, the use of a decontamination apparatus used in the decontamination step eliminates the need for providing a decontamination apparatus separately, and further reduces the burden of treating the concentrated water in terms of cost of the apparatus.
In the present invention, in the electrolytic step, acidic water is obtained from the anode side, and the acidic water after the reverse osmosis membrane is sterilized and washed with the acidic water, or the acidic water as it is obtained in the electrolytic step. It is preferable to perform the neutralization process which adds and neutralizes to alkaline water which the metal component isolate | separated by the said precipitate separation process.
Alkaline water from which the precipitated metal component is separated is usually neutralized and disposed of through the precipitate separation process. In this method, since acidic water obtained at the anode side in the electrolytic process is used as the neutralizing solution. In addition, it is not necessary to prepare or generate acidic water separately, so that the burden of treating the generated concentrated water can be further reduced.
Moreover, it is preferable that it is an apparatus which deposits by filtration using an MF membrane or an UF membrane as said depositing apparatus.
In such a method, since a metallurgical component using a MF membrane or an UF membrane can separate the precipitated metal components relatively easily, the burden of treating the concentrated water can be further reduced.
Moreover, in this invention, it is preferable to make pH of the said alkaline water into 9-14.
In such a method, by setting the pH of the alkaline water to 9 or more, the metal component can be sufficiently precipitated, and the precipitated metal component can be sufficiently separated by the smelting apparatus, so that the burden of treating the concentrated water can be further reduced. . Moreover, if it is pH14 or less, the possibility of damaging a degreasing apparatus (for example, MF membrane etc.) is also reduced.
Moreover, this invention is a purification | cleaning apparatus of the metal component containing water which has the reverse osmosis membrane separation apparatus which isolate | separates the metal component containing water which the metal component melt | dissolves into the purified water which is permeate water, and concentrated water by a reverse osmosis membrane, And an electrolytic device which electrolyzes the concentrated water to obtain alkaline water at the cathode side, and a precipitate separation device for filtering and separating the metal component precipitated by being alkaline from the alkaline water obtained by the electrolytic device. It is to provide an apparatus for purifying water containing water.
As mentioned above, according to this invention, the processing burden of the concentrated water produced | generated by the reverse osmosis membrane separation can be reduced at least.
BRIEF DESCRIPTION OF THE DRAWINGS It is a schematic flowchart which shows the apparatus and method for purifying the metal-containing water of one embodiment.
Best Mode for Carrying Out the Invention
EMBODIMENT OF THE INVENTION Hereinafter, embodiment of this invention is described, referring drawings.
First, the purification processing apparatus of metal component containing water is demonstrated.
1 is a schematic flow chart in a purification treatment apparatus for metal component-containing water of the present embodiment.
The purification | cleaning apparatus of the metal component containing water of this embodiment is the
The
As raw water (A), sewage, biological treatment water of sewage, factory drainage, groundwater, river water, landfill leachate, seawater, etc. are mentioned, for example.
Moreover, calcium, magnesium, iron, aluminum etc. are mentioned as a metal component contained in these raw water (A).
The said
As this filtration member, the filtration member provided with the
Preferably, it comprises the
On the other hand, in the present specification, filtration means rougher filtration than reverse osmosis membrane filtration, that is, it is performed before separation of the reverse osmosis membrane, and means that coarse impurities are removed rather than separation with the reverse osmosis membrane.
In the purification treatment apparatus of the present embodiment, the treatment treatment water deposited in the
In addition, if necessary, the treated water and the like are flowed back into the depositing
The reverse osmosis
The permeate water (B) is usually set to an electrical conductivity of 200 µS / cm or less, preferably 50 µS / cm or less. The concentrated water (C) has an electrical conductivity of 3000 to 15000 µS / cm, preferably 5000 to 10000 µS / cm.
In the purification apparatus of the present embodiment, the permeated water B is discharged to the outside of the system by piping, and the concentrated water C is supplied to the
Specifically, the electrolytic apparatus is provided with the concentrated
The
The
In the
The said alkaline water (D) is adjusted so that pH may be 9-14 normally, Preferably pH is 10-12.
In the purification processing apparatus of the present embodiment, the alkaline water D is further supplied to the precipitate
In detail, the alkaline
In addition, when the alkaline water D stored in the alkaline
The depositing
In the purification processing apparatus of this embodiment, the alkaline water D from which the precipitated metal component is separated is supplied to the
In addition, the above-mentioned
On the other hand, the backwash waste liquid (F) containing the metal component discharged | emitted out of the system at high concentration will be water-processed by the conventionally well-known method.
In this embodiment, as a metal component precipitated from alkaline water (D), calcium, magnesium, iron, aluminum etc. are mentioned, for example, These are calcium carbonate, magnesium carbonate, iron hydroxide, hydroxide hydroxide, for example. Precipitates in an inorganic salt state such as aluminum.
In the purification processing apparatus of the present embodiment, the acidic water E is further supplied to the reverse osmosis
Specifically, a reverse osmosis membrane is provided through a pipe having an acidic
On the other hand, when the acidic water E stored in the acidic
In the purification processing apparatus of the present embodiment, the acidic water E supplied to the reverse osmosis
In the
In addition, the neutralized water G neutralized in the
On the other hand, the neutralized water G discharged out of the system is subjected to water treatment by a conventionally known method.
In this embodiment, since the acidic water E is supplied to the reverse osmosis
Here, the said acidic water (E) is adjusted so that pH may be 1-5 normally, Preferably pH is 2-4.
If it is such pH, sufficient scale removal and sterilization can be performed, without causing a big damage to the
The purification processing apparatus of the metal component containing water of this embodiment is as above-mentioned, Next, the purification processing method of the metal component containing water of this embodiment is demonstrated.
In the purification treatment method of the present embodiment, a reverse osmosis membrane is used for depositing a raw water (A), which is a metal component-containing water in which a metal component is dissolved, in a depositing device (20), and a deposit treated water deposited in the depositing step. Reverse osmosis membrane separation step of separating permeate water (B) into purified water and concentrated water (C) by separation, and electrolytically decomposing the concentrated water (C) to obtain alkaline water (D) on the cathode side. Purification of the electrolytic step of obtaining acidic water (E) from the precipitate, the precipitate separation step of filtering and separating the metal component precipitated by being alkaline from the alkaline water (D) obtained in the electrolytic step, and the metal component separated by filtration by back washing. Neutralization ball which removes from the
In this embodiment, since the precipitated metal separation process separates the precipitated metal component and performs the wastewater treatment for the backwashing waste liquid containing the metal component at a high concentration, the amount of water that is the object of the wastewater treatment ) Can be reduced, and the processing burden can be significantly reduced.
In the above-mentioned purification step, suspension components such as mud contained in the raw water (A) are removed by, for example, membrane filtration.
By such a process, the possibility that the
In the reverse osmosis membrane separation step, the raw water (A) from which the suspending component is removed by the depuration step is separated into permeate water (B) and concentrated water (C) in which the metal component is concentrated by reverse osmosis membrane separation.
In this embodiment, since the
As the permeate water (B), the electrical conductivity is usually 200 µS / cm or less, preferably 50 µS / cm or less. In addition, as said concentrated water (C), electrical conductivity is made into 3000-15000 microS / cm normally, Preferably you may be 5000-10000 microS / cm.
In the said electrolytic process, the concentrated water (C) produced | generated by the reverse osmosis membrane process is isolate | separated into alkaline water (D) of a cathode side, and acidic water (E) of a positive electrode side by electrolysis.
The voltage applied at the time of electrolysis is 1-5V normally, Preferably it is 2-3V.
By setting it as such a voltage, concentrated water C can be fully electrolyzed.
In addition, the time of electrolysis is not specifically limited, It continues until the pH of alkaline water (D) is 9-14 and the pH of acidic water (E) becomes 1-5.
By making alkaline water (D) into such pH, the metal component contained can fully be precipitated.
Moreover, when acidic water (E) is made into such pH, when the
In the precipitate separation step, the metal component precipitated by being alkaline from the alkaline water (D) obtained in the electrolytic step is separated by filtration.
Specifically, metal components such as calcium, magnesium, iron and aluminum precipitated in an inorganic salt state such as calcium carbonate, magnesium carbonate, iron hydroxide and aluminum hydroxide are separated using the
In the said neutralization process, alkaline water (D) and the acidic water (E) which passed through the said precipitate separation process are supplied to the
In the present embodiment, the neutralized water (G) obtained in the neutralization step is mixed with the raw water (A) and subjected to the same treatment again with the raw water (A), or discharged to the outside of the system via the backwash waste liquid storage tank (23). Or
Although the purification processing apparatus and purification processing method of the metal component containing water in this embodiment are as above-mentioned, The purification processing apparatus and purification treatment method of the metal component containing water of this invention are not limited to the said embodiment, It is design change suitably. This is possible.
For example, in the purification treatment method of the present embodiment, in the neutralization step, a washing waste liquid obtained by acid-cleaning the
Moreover, in the purification processing apparatus of the metal component containing water of this embodiment, the backwash waste
Moreover, in the purification processing apparatus of the metal component containing water of this embodiment, although the
20... A depositing device
30. Reverse osmosis membrane separation device
40…. Electrolytic device
50…. Precipitate separation device
Claims (6)
Further, an electrolytic step of electrolyzing the concentrated water to obtain alkaline water at the cathode side, and a precipitate separation step of filtration-separating the metal component precipitated by being alkaline from the alkaline water obtained in the electrolytic step, characterized by the above-mentioned. Method for purifying metal-containing water.
A depositing step of depositing the metal component-containing water before the reverse osmosis membrane separation step in a depositing apparatus is carried out. In the reverse osmosis membrane separation step, the reverse osmosis membrane separation of the metal component-containing water deposited in the depositing step is performed. In the precipitate separation step, the metal component-containing water purifying treatment method of separating the precipitated metal component in the above-mentioned depositing device.
In the electrolytic step, acidic water is obtained on the anode side, and the acidic water after the reverse osmosis membrane is sterilized and washed with the acidic water, or the acidic water as obtained in the electrolytic step is subjected to the metal component by the precipitate separation step. A method for purifying a metal component-containing water, which carries out a neutralization step of adding to the separated alkaline water and neutralizing it.
A method for purifying a metal component-containing water, wherein the depositing apparatus is an apparatus for depositing by filtration using an MF membrane or an UF membrane.
The purification method of the metal component containing water which makes pH of the said alkaline water into 9-14.
A metal comprising: an electrolytic device that electrolyzes the concentrated water to obtain alkaline water at the cathode side, and a precipitate separation device that filters and separates the metal component precipitated by being alkaline from the alkaline water obtained by the electrolytic device. Purification processing apparatus of component containing water.
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
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JPJP-P-2008-091213 | 2008-03-31 | ||
JP2008091213 | 2008-03-31 | ||
JPJP-P-2008-318350 | 2008-12-15 | ||
JP2008318350A JP5564174B2 (en) | 2008-03-31 | 2008-12-15 | Purification method and apparatus for purification of water containing metal components |
Publications (1)
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KR20100134553A true KR20100134553A (en) | 2010-12-23 |
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KR1020107016452A KR20100134553A (en) | 2008-03-31 | 2009-03-04 | Method of purifying water containing metallic ingredient and apparatus for purification |
Country Status (6)
Country | Link |
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JP (1) | JP5564174B2 (en) |
KR (1) | KR20100134553A (en) |
CN (1) | CN101945826B (en) |
BR (1) | BRPI0906347A8 (en) |
TW (1) | TWI438153B (en) |
WO (1) | WO2009122847A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
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KR101360020B1 (en) * | 2013-03-15 | 2014-02-12 | 재단법인 한국계면공학연구소 | Preprocessing of membrane filtration and system using the same |
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JP5609439B2 (en) * | 2010-08-31 | 2014-10-22 | 株式会社Ihi | Carbon dioxide fixing method and carbon dioxide fixing device |
JP5824793B2 (en) * | 2010-09-10 | 2015-12-02 | 株式会社Ihi | Magnesium recovery method and magnesium recovery device |
CN102210978B (en) * | 2011-03-14 | 2014-03-05 | 四川科伦药业股份有限公司 | Method and reagent for cleaning and repairing discarded reverse osmosis film in offline mode |
CN102179180B (en) * | 2011-03-14 | 2013-05-15 | 四川科伦药业股份有限公司 | Off-line washing and repairing device for multifunctional waste reverse osmosis membrane |
JP2013169511A (en) * | 2012-02-21 | 2013-09-02 | Toshiba Corp | Membrane filtration system |
CN102765838B (en) * | 2012-08-01 | 2014-02-26 | 威洁(石狮)中水回用技术有限公司 | Heavy metal extraction and water purification integrated device |
JP6158658B2 (en) * | 2012-10-02 | 2017-07-05 | 株式会社日本トリム | Purified water production equipment |
CN104787938B (en) * | 2015-03-31 | 2017-10-24 | 宁波方太厨具有限公司 | It is a kind of effectively to remove the electrolyzed water machines of removing heavy metals |
CN110627268A (en) * | 2019-09-28 | 2019-12-31 | 珠海市江河海水处理科技股份有限公司 | Environment-friendly seawater desalination system and process thereof |
CN111559786A (en) * | 2020-05-28 | 2020-08-21 | 佛山市顺德区美的饮水机制造有限公司 | Water purifier and water purifier |
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JPH06304452A (en) * | 1993-04-26 | 1994-11-01 | Nitto Denko Corp | Method for treating of liquid and electrodeposition apparatus used in this method |
JPH09323029A (en) * | 1996-06-05 | 1997-12-16 | Nitto Denko Corp | Water desalting method and device therefor |
JP2001335660A (en) * | 2000-05-30 | 2001-12-04 | Ube Ind Ltd | Recycling method of organic waste materials including vinyl chloride resin |
JP2003103259A (en) * | 2001-09-28 | 2003-04-08 | Vision:Kk | Method for cleaning filter and reverse osmosis membrane |
JP3884407B2 (en) * | 2003-06-03 | 2007-02-21 | 株式会社東芝 | Method and apparatus for treating fluorine-containing water |
JP2005211780A (en) * | 2004-01-29 | 2005-08-11 | Koken Ltd | Electrolyzed water generator |
JP4628033B2 (en) * | 2004-07-29 | 2011-02-09 | アサヒプリテック株式会社 | Method for recovering Au from an aqueous solution containing cyanide |
JP4578228B2 (en) * | 2004-12-21 | 2010-11-10 | アサヒプリテック株式会社 | Method for recovering Au from an aqueous solution containing cyanide |
JP2006272031A (en) * | 2005-03-28 | 2006-10-12 | Toto Ltd | Apparatus for producing drinking water |
CN101024537A (en) * | 2006-02-23 | 2007-08-29 | 王俊川 | Electric-plating waste water recovering and utilizing process and apparatus |
JP5019422B2 (en) * | 2006-10-19 | 2012-09-05 | オルガノ株式会社 | Domestic water supply method and apparatus |
JP2009195808A (en) * | 2008-02-20 | 2009-09-03 | Nippon Steel Corp | Circulating water reuse apparatus and reuse method in cooling system for open circulating system |
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2008
- 2008-12-15 JP JP2008318350A patent/JP5564174B2/en active Active
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2009
- 2009-03-04 BR BRPI0906347A patent/BRPI0906347A8/en not_active Application Discontinuation
- 2009-03-04 CN CN200980104815.1A patent/CN101945826B/en not_active Expired - Fee Related
- 2009-03-04 KR KR1020107016452A patent/KR20100134553A/en not_active Application Discontinuation
- 2009-03-04 WO PCT/JP2009/054027 patent/WO2009122847A1/en active Application Filing
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Cited By (1)
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KR101360020B1 (en) * | 2013-03-15 | 2014-02-12 | 재단법인 한국계면공학연구소 | Preprocessing of membrane filtration and system using the same |
Also Published As
Publication number | Publication date |
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JP5564174B2 (en) | 2014-07-30 |
CN101945826A (en) | 2011-01-12 |
JP2009262124A (en) | 2009-11-12 |
TWI438153B (en) | 2014-05-21 |
WO2009122847A1 (en) | 2009-10-08 |
BRPI0906347A8 (en) | 2019-01-29 |
BRPI0906347A2 (en) | 2016-08-09 |
TW200946462A (en) | 2009-11-16 |
CN101945826B (en) | 2013-05-01 |
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