WO2012103582A1 - Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions - Google Patents
Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions Download PDFInfo
- Publication number
- WO2012103582A1 WO2012103582A1 PCT/AU2012/000083 AU2012000083W WO2012103582A1 WO 2012103582 A1 WO2012103582 A1 WO 2012103582A1 AU 2012000083 W AU2012000083 W AU 2012000083W WO 2012103582 A1 WO2012103582 A1 WO 2012103582A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- water
- removal
- aqueous solutions
- accordance
- water soluble
- Prior art date
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Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/24—Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3085—Chemical treatments not covered by groups B01J20/3007 - B01J20/3078
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/286—Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08B—POLYSACCHARIDES; DERIVATIVES THEREOF
- C08B5/00—Preparation of cellulose esters of inorganic acids, e.g. phosphates
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08H—DERIVATIVES OF NATURAL MACROMOLECULAR COMPOUNDS
- C08H8/00—Macromolecular compounds derived from lignocellulosic materials
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J3/00—Processes of treating or compounding macromolecular substances
- C08J3/12—Powdering or granulating
- C08J3/14—Powdering or granulating by precipitation from solutions
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08L—COMPOSITIONS OF MACROMOLECULAR COMPOUNDS
- C08L1/00—Compositions of cellulose, modified cellulose or cellulose derivatives
- C08L1/08—Cellulose derivatives
- C08L1/16—Esters of inorganic acids
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2220/00—Aspects relating to sorbent materials
- B01J2220/40—Aspects relating to the composition of sorbent or filter aid materials
- B01J2220/48—Sorbents characterised by the starting material used for their preparation
- B01J2220/4812—Sorbents characterised by the starting material used for their preparation the starting material being of organic character
- B01J2220/4825—Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2220/00—Aspects relating to sorbent materials
- B01J2220/40—Aspects relating to the composition of sorbent or filter aid materials
- B01J2220/48—Sorbents characterised by the starting material used for their preparation
- B01J2220/4812—Sorbents characterised by the starting material used for their preparation the starting material being of organic character
- B01J2220/4825—Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
- B01J2220/4831—Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton having been subjected to further processing, e.g. paper, cellulose pulp
-
- 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
- C02F2101/103—Arsenic compounds
-
- 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
- C02F2101/106—Selenium compounds
-
- 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
-
- 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
- C02F2101/206—Manganese or manganese compounds
-
- 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
- C02F2101/22—Chromium or chromium compounds, e.g. chromates
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2301/00—Characterised by the use of cellulose, modified cellulose or cellulose derivatives
- C08J2301/08—Cellulose derivatives
- C08J2301/16—Esters of inorganic acids
Definitions
- This invention relates to a chemical process for synthesising a modified cellulose phosphate powder from biomass sou roes of oetlulose Including, but not limited to, algae, bagasse, and waste paper.
- This invention further relates to the application of the cellulose phosphate powder for use in removel of various contaminants or chemical species from water. Including but not limited to Mercury, Cadmium, Chromium, Copper, Zinc, Iron, Bismuth, Selenium, Tin, Cobalt, Nickel, Vanadium, Manganese, Uranium, Thorium, Arsenic, Load and Ammonia.
- This Invention has particular application in near neutral pH aqueous solutions that are contaminated with various water soluble species.
- Typical species include those containing transition metals, and also other contaminants containing ammonia, arsenic, and selenium. At low concentrations these contaminants are soluble in water and often have toxicological, clinical or environmental impacts. At low concentrations, many contaminants are difficult to separate from water.
- the existing solutions for removal of trace level contaminants, particularly those utilized in industrial applications include the use of ion exchange resins, activated carbon or alumina, or titanium dioxide, reverse osmosis, chemical precipitation, or biological filtration. Each of these works with only specific contaminants. However none of these options is satisfactory for all contaminants. Further, other limitations of these processes include insufficient removal of particular contaminants, impractical application for large volumes, and high expense. Often a combination of two or more techniques is necessary, and creates process engineering difficulties.
- the present invention involves creating a modified cellulose based powder by reacting a biomass based celiuloslc raw material with dilute phosphoric acid at elevated temperature.
- the cellulosic raw material is partially dissolved and then the remaining insoluble raw material is separated from the dilute phosphoric add solution.
- the clear phosphoric acid solution is then neutralized with subsequent precipitation of the modified cellulose, followed by , separating, washing and removal of excess water prior to use.
- the resulting product is a sorbent powder.
- sorbent (Wherever the term "sorbent* is used in this specification, this shall be Interpreted to mean adsorbent However, It is to be understood that the product may also have absorbent properties.)
- the sorbent product which may be in the form of a powder or a slurry, is particularly useful for removal of low levels of contaminants from water and aqueous solutions. The solid residue resulting from extraction is then inert and non flammable, and the remaining filtrate is discarded, or may be processed for recovery of unreacted phosphoric acid .
- the method of application includes but is not limited to contacting the sorbent product with the contaminated water or aqueous solution by mixing and then separating either by allowing the product to settle and decanting the supernatant treated water or solution, or by filtering, or some other method of solid liquid separation.
- sorbent product can be used as an active component in a filter or permeable reactive barrier
- the synthesis of the sorbent powder is performed by utilizing a ceilulosic feedstock.
- a ceilulosic feedstock This may include but is not Hmfted to algae, bagasse, and favourably, waste paper.
- the ceilulosic feedstock is then mixed with dilute phosphoric acid (typically in the concentration range from approximately 2g/ ⁇ up to 40 g/l but may also be In the range 1g/I up to 80g/[), and heated to reaction temperature for at least 2 minutes, but more preferably at least 5 minutes, up to 4 hours.
- the heating may be performed by conventional means, but may also include alternative heating technologies for water Including microwave heating.
- the ratio of ceilulosic feedstock to dilute phosphoric acid may typically be between a ratio of 1 part feedstock to 5 parts dilute phosphoric acid, up to 1 part feedstock to 40 parts of dilute phosphoric acid. However, this ratio may also foreseeabiy be in the range of 1 part feedstock to 2 parts dilute phosphoric acid , up to 1 part feedstock to 80 parts of dilute phosphoric acid. This is more of a practical issue rather than a technical limit.
- the yield of sorbent from feedstock ranges from 4% by weight up to 40% by weight depending upon the feedstock used, the dilute acid concentration and volume, and the temperature and heating time of the synthesis.
- the remaining solids and the solution are separated by any suitable means. Simple filtering has been shown to be effective.
- the solid residue consists of insoluble end unreactive ceilulosic -feedstock. This residue is non flammable and, based upon this characteristic, may be useful as a tire retardant and in insulation products.
- the filtrate or supernatant la neutralized to pH 7 with any suitable neutraizing agent but preferably caustic soda. As the neutralization is performed, a fine precipitate develops in solution which settles easily and filters easily. This precipitate is the object of the process and is recovered by filtering or other suitable solid liquid separation technique. The precipitate is then washed with water to remove any remaining salts, and excess water removed. Accordingly, the product may be a dried powder or may be in the form of a slurry.
- the application of the sorbent product for treatment of low level water contaminants is performed by simple mixing of the sorbent product with water. Contact and mixing time may typically be between approximately 5 minutes and 2 hours. However, this range may be greater and foreseeably may be between approximately 2 minutes and 24 hours, with dose rate determined by total load of contaminants and capacity of the sorbent for a given contaminant.
- solid liquid separation is performed by any suitable means including but not limited to tittering, centrifugation, and decanting. Additionally the sorbent can be utilized as a filter bed with the contaminated water passed through the filter bed with removal of various contaminants taking place within the filter bed.
- the present invention provides an alternative and more cost effective solution for the removal of the abovementioned contaminants from water.
- the cellulose phosphate product has different physical characteristics and improved performance as water treatment product, particularly for trace contaminants, in addition, the cellulose phosphate of the present invention has a Fourier Transformation Infrared spectrum that shows significant differences from conventional cellulose phosphate esters and ethers.
- the process described in the present invention utilizes a different method of synthesis to previously taught approaches and otters a number of advantages including greater simplicity, tower risk and production costs. This results In a product with affinity for a range of contaminants (the affinity of which may vary according to the contaminant) without the need for further functionalization.
- Example 1 3.128 g of waste paper was reacted with 120 mis of 8% w/v phosphoric acid at 104 degrees C for 2hours 43 minutes. The resultant mixture was cooled, separated by filtering end the residue washed and dried. 2.206 g of residue was recovered. The filtrate and washings were neutralized with 40 g/l caustic soda to a pH of 7.0, the resultant precipitated powder was filtered and washed and dried to give a final weight of 0.845 g of sorbent powder. 0.5g of this powder was added to a 1 litre water sample with 24 hours mixing and the resultant change in composition was:
- Example 2 2.003 g of bagasse was reacted with 100 mis of 8% w/v phosphoric acid at 100 degrees C for 3 hours and 15 minutes. The resultant mixture was cooled separated by filtering and the residue washed and dried. 1.782 g of residue was recovered. The filtrate and washings were neutralized with 40 g/l caustic soda to a pH of 7.0, the resultant precipitated powder was filtered and washed and dried to give a final weight of 0.241 g of sorbent powder.
- Example 3 1.030 g of dried filamentous algae was reacted with 100 mis of 8% w/v phosphoric acid at 100 degrees C for 3 hours and 15 minutes. The resultant mixture was cooled separated by filtering and the residue washed and- dried. 0.962 g of residue was recovered. The filtrate end washings were neutralized with 40 g/l caustic soda to a pH of 7.0, the resultant precipitated powder was filtered and washed and dried to give a final weight of 0.073 g of sorbent powder.
- Example 4 1170 g of waste paper was boiled with 23.3 litres of 4.4% w/v phosphoric acid for 2 hours. The resultant mixture was cooled separated by deoanting end then filtering and the residue washed and dried. The filtrate and washings were neutralized with 80 g/l caustic soda to a pH of 6.5, the resultant precipitated powder was filtered and washed and dried to give a final weight of 221 g of sorbent powder. 339 mg of this powder was prepared as a column filter and 100 ml of contaminated water was passed through the filter. The resultant change in water composition was:
- the invention enables the reduction of a range of trace contaminants from contaminated water sources with near neutral pH. without any toxic or aesthetic reduction In water quality.
- This invention has particular application in dilute waste water treatment, or environmental water treatment
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- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Medicinal Chemistry (AREA)
- Polymers & Plastics (AREA)
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- Materials Engineering (AREA)
- Inorganic Chemistry (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Polysaccharides And Polysaccharide Derivatives (AREA)
- Water Treatment By Sorption (AREA)
Abstract
Description
Claims
Priority Applications (9)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CA2828777A CA2828777A1 (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions |
SG2013065644A SG193010A1 (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions |
JP2013552063A JP6076264B2 (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder product, process for producing the same, and use for removing contaminants from aqueous solutions |
EP12742299.6A EP2670711A4 (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions |
BR112013019640-8A BR112013019640A2 (en) | 2011-02-01 | 2012-02-01 | processes for producing a cellulose-based absorbent material, cellulose-based absorbent products and methods for removing water-soluble contaminants from water and other aqueous solutions |
AU2012212392A AU2012212392A1 (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions |
CN201280017492.4A CN103476710B (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder-product and manufacture method thereof and from aqueous solution, remove the application of pollutant |
EA201370173A EA201370173A1 (en) | 2011-02-01 | 2012-02-01 | PRODUCT FROM POWDER OF PHOSPHATE OF CELLULOSE AND METHOD FOR ITS PREPARATION AND ALSO APPLICATION FOR REMOVAL OF POLLUTANT IMPURITIES FROM AQUEOUS SOLUTIONS |
US13/983,225 US9694343B2 (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AU2011900307A AU2011900307A0 (en) | 2011-02-01 | Cellulose phosphate powder product and process for the manufacture thereof, and application to removal of contaminants from water | |
AU2011900307 | 2011-02-01 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2012103582A1 true WO2012103582A1 (en) | 2012-08-09 |
Family
ID=46602007
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/AU2012/000083 WO2012103582A1 (en) | 2011-02-01 | 2012-02-01 | Cellulose phosphate powder product and process for manufacture thereof, and application to removal of contaminants from aqueous solutions |
Country Status (12)
Country | Link |
---|---|
US (1) | US9694343B2 (en) |
EP (1) | EP2670711A4 (en) |
JP (1) | JP6076264B2 (en) |
CN (1) | CN103476710B (en) |
AU (1) | AU2012212392A1 (en) |
BR (1) | BR112013019640A2 (en) |
CA (1) | CA2828777A1 (en) |
CL (1) | CL2013002208A1 (en) |
EA (1) | EA201370173A1 (en) |
PE (1) | PE20140631A1 (en) |
SG (2) | SG193010A1 (en) |
WO (1) | WO2012103582A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
ES2659296A1 (en) * | 2016-09-14 | 2018-03-14 | Universidad De Valladolid | MULTILECHE PILOT PROCESS AND PLANT FOR BIOMASS FRACTIONATION (Machine-translation by Google Translate, not legally binding) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111790357A (en) * | 2020-07-22 | 2020-10-20 | 广东药科大学 | Preparation method of modified traditional Chinese medicine residue biomass adsorbent and application of modified traditional Chinese medicine residue biomass adsorbent in treatment of dye wastewater |
CN113831795A (en) * | 2021-09-26 | 2021-12-24 | 齐耐润工业设备(上海)有限公司 | Teflon coated metal net and preparation method thereof |
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-
2012
- 2012-02-01 EA EA201370173A patent/EA201370173A1/en unknown
- 2012-02-01 EP EP12742299.6A patent/EP2670711A4/en not_active Withdrawn
- 2012-02-01 WO PCT/AU2012/000083 patent/WO2012103582A1/en active Application Filing
- 2012-02-01 JP JP2013552063A patent/JP6076264B2/en not_active Expired - Fee Related
- 2012-02-01 SG SG2013065644A patent/SG193010A1/en unknown
- 2012-02-01 SG SG10201600783UA patent/SG10201600783UA/en unknown
- 2012-02-01 US US13/983,225 patent/US9694343B2/en not_active Expired - Fee Related
- 2012-02-01 AU AU2012212392A patent/AU2012212392A1/en not_active Abandoned
- 2012-02-01 BR BR112013019640-8A patent/BR112013019640A2/en not_active IP Right Cessation
- 2012-02-01 PE PE2013001731A patent/PE20140631A1/en not_active Application Discontinuation
- 2012-02-01 CA CA2828777A patent/CA2828777A1/en not_active Abandoned
- 2012-02-01 CN CN201280017492.4A patent/CN103476710B/en not_active Expired - Fee Related
-
2013
- 2013-08-01 CL CL2013002208A patent/CL2013002208A1/en unknown
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GB899284A (en) * | 1957-11-01 | 1962-06-20 | Atomic Energy Authority Uk | Improved phosphorylated cellulose and method of obtaining it |
GB1001603A (en) | 1961-04-10 | 1965-08-18 | Fmc Corp | Separation, purification and recovery processes |
GB1445754A (en) * | 1972-11-20 | 1976-08-11 | Elepon Kakoki Co | Method of adsorbing heavy metal ions |
JPS58161926A (en) * | 1982-03-18 | 1983-09-26 | Sumitomo Chem Co Ltd | Method for recovering uranium |
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Also Published As
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US20140073775A1 (en) | 2014-03-13 |
JP6076264B2 (en) | 2017-02-08 |
JP2014505592A (en) | 2014-03-06 |
CN103476710A (en) | 2013-12-25 |
EA201370173A1 (en) | 2014-01-30 |
CN103476710B (en) | 2016-12-28 |
AU2012212392A1 (en) | 2013-05-09 |
US9694343B2 (en) | 2017-07-04 |
BR112013019640A2 (en) | 2020-08-04 |
CL2013002208A1 (en) | 2014-06-27 |
SG10201600783UA (en) | 2016-03-30 |
SG193010A1 (en) | 2013-09-30 |
EP2670711A1 (en) | 2013-12-11 |
CA2828777A1 (en) | 2012-08-09 |
EP2670711A4 (en) | 2017-03-29 |
PE20140631A1 (en) | 2014-05-29 |
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