WO1995027753A1 - Improved polyethylene terephthalate decontamination - Google Patents
Improved polyethylene terephthalate decontamination Download PDFInfo
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- WO1995027753A1 WO1995027753A1 PCT/AU1995/000201 AU9500201W WO9527753A1 WO 1995027753 A1 WO1995027753 A1 WO 1995027753A1 AU 9500201 W AU9500201 W AU 9500201W WO 9527753 A1 WO9527753 A1 WO 9527753A1
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- pet
- ethanediol
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- 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
- C08J11/00—Recovery or working-up of waste materials
- C08J11/04—Recovery or working-up of waste materials of polymers
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- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C51/00—Preparation of carboxylic acids or their salts, halides or anhydrides
- C07C51/09—Preparation of carboxylic acids or their salts, halides or anhydrides from carboxylic acid esters or lactones
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C67/00—Preparation of carboxylic acid esters
- C07C67/03—Preparation of carboxylic acid esters by reacting an ester group with a hydroxy group
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- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08G—MACROMOLECULAR COMPOUNDS OBTAINED OTHERWISE THAN BY REACTIONS ONLY INVOLVING UNSATURATED CARBON-TO-CARBON BONDS
- C08G63/00—Macromolecular compounds obtained by reactions forming a carboxylic ester link in the main chain of the macromolecule
- C08G63/88—Post-polymerisation treatment
- C08G63/90—Purification; Drying
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- 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
- C08J2327/00—Characterised by the use of homopolymers or copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and at least one being terminated by a halogen; Derivatives of such polymers
- C08J2327/02—Characterised by the use of homopolymers or copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and at least one being terminated by a halogen; Derivatives of such polymers not modified by chemical after-treatment
- C08J2327/04—Characterised by the use of homopolymers or copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and at least one being terminated by a halogen; Derivatives of such polymers not modified by chemical after-treatment containing chlorine atoms
- C08J2327/06—Homopolymers or copolymers of vinyl chloride
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- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/143—Feedstock the feedstock being recycled material, e.g. plastics
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- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Definitions
- the present invention relates to a method for the decontamination of polyethylene terephthalate (“PET”) components at reduced temperature.
- PET polyethylene terephthalate
- the invention also proposes a method for separating PET components from other materials.
- PET is a thermoplastic polyester that can be formed from 1:2 ethanediol and terephthalic acid by direct esterification to form bis (hydroxy ethyl) terephthalate ester ("BHT") which is then polymerised by catalysed ester exchange to useful polymers.
- BHT bis (hydroxy ethyl) terephthalate ester
- PET has been used extensively because it can be offered as an oriented film or fibre, has high tenacity, good electrical resistance and low moisture absorption together with a melting point of approximately 265 degrees Celsius.
- PCT/AU93/00198 represents a significant advance in the decontamination of PET-containing substances
- subsequent investigations have revealed that at or about the atmospheric boiling point of ethanediol, the non-PET substances, such as paper and PVC, may be adversely affected.
- PVC in particular, may be chemically degraded in such a way as to alter its ability to be commercially recovered.
- PVC in particular, may be chemically degraded in such a way as to alter its ability to be commercially recovered.
- PVC in particular, may be chemically degraded in such a way as to alter its ability to be commercially recovered.
- the boiling point of ethanediol PVC is severely degraded as it is dehydrochlorinated which yields a brown brittle product.
- the resultant brown product is not suitable for re-extrusion to make commercially useful recycled products. Consequently, further investigation have been directed towards the process of PET decontamination with the view of balancing the need for adequate embrittlement of
- a process for removing contaminants from PET components by depolymerising PET including the following steps: (a) transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET;
- the invention further provides a process for removing contaminants from PET components by depolymerising PET, including the following steps: (a) transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET;
- the invention further provides a process for separating PET components from other materials, including the following steps:
- the alkanediol or alkanediols are selected from the group including ethanediol, 1:4 butanediol and 1:6 hexanediol and mixtures thereof.
- Ethanediol is particularly preferable as it is one of the monomers used in the direct esterification to form PET.
- the use of alkanediols other than ethanediol therefore introduces into the reaction a substance which must ultimately be separated.
- the temperature of the alkanediol or alkanediols used in steps (a) above in the transesterification of the PET component is preferably in the range of 130 degrees Celsius to within 10 degrees Celsius of the boiling point of ethanediol and is particularly preferred to be in the range of 140 degrees Celsius to 160 degrees Celsius. This latter temperature range is preferred when separation of PVC or other non-PET components is desired for re ⁇ use. This will significantly avoid degradation of PVC by dehydrochlorination which poses problems with the re-use of PVC. The release of hydrogen chloride in the reactor is also substantially eliminated.
- the predetermined time for embrittlement may commercially lie in the range of up to 150 minutes although, of course, longer times may still achieve the desired level of embrittlement of PET without adverse effect upon contaminants.
- embrittlement is caused to occur within a period of between 30 minutes and 120 minutes and more preferably, between 45 minutes and 60 minutes.
- the transesterification giving embrittlement is preferably controlled by both temperature and time to give a brittle product with minimum over treatment. This can be effected by using plug flow reactors with a narrow range of residence times. However, if the residence time is not critical to the cost of the process then there is no technical limitation on residence time. It is anticipated that most process designers will select a residence time between 45 and 60 minutes to enable the use of a smaller sized plant.
- transesterification catalysts to the alkanediol or alkanediols further reduces the temperature or time necessary to achieve the required embrittlement. This is particularly useful if the time for embrittlement is uneconomical and the addition of catalyst can reduce the time to an economic residence time. Alternatively, the reduced reaction temperature can be valuable if a reduced vapour pressure of ethanediol is to be used, or temperatures which degrade other useful substances mixed with PET are to be avoided.
- the addition of catalyst to the mixture for transesterification supplements the small pre-existing concentration of catalyst in the feed stock PET, residual from the original polymerisation.
- the transesterification catalyst may be the known useful transesterification catalysts selected from the group including antimony (HI) oxide, antimony (HI) acetate, germanium dioxide, manganese acetate, terra butoxy titanium and mixtures thereof.
- HI antimony
- HI antimony
- germanium dioxide germanium dioxide
- manganese acetate manganese acetate
- terra butoxy titanium magnesium oxide
- any of the known transesterification catalysts would have a similar action, but may be less acceptable to consumers as coloured by ⁇ products are generated by the other disclosed catalysts.
- Embrittlement which takes place prior to the collapse of the original PET structure allows the PET to be crushed to separate it from the contaminants. This allows separation to take place on the basis of size and density. Crushing to a diameter of less than 1 millimetre is preferred. Crushing can be achieved by rollers or hammer mills or any other known techniques for reducing the size of particles. Once crushed, the PET is separated from typical contaminants such as hydrocarbons and pigments from paper. Other substances giving rise to coloured products can be separated by screening, washing or density separation from other contaminants which have not become embrittled. A number of substances such as Nylons dissolve in the hot alkanediols and are removed with the liquid alkanediol. Preferably, the uncrushed material includes PVC.
- the temperature of the alkanediol or alkanediols in the transesterification of the crushed PET which form a solution of short chain PET polymers and BHT is within the range of between at or about the boiling point of ethanediol (preferably within 5 or 10 degrees Celsius of the boiling point of ethanediol) and 240 degrees Celsius. In a particularly preferred form of the invention, the temperature range is between 220 degrees Celsius and 240 degrees Celsius.
- the alkanediols are selected from the group including ethanediol, 1:4 butanediol and 1:6 hexanediol and mixtures thereof. Ethanediol is most preferred.
- separation of the PET rich fraction in one preferred form of the invention can take place by filtration methods and more preferably by high pressure filtration methods.
- the addition of activated carbon or a combination of activated carbon and activated clay is used as an adsorbent for a wide variety of molecules such as dyes, pesticides, coloured polymers, etc. If alkanediols other than ethanediol have been used, they can also be removed at this time by known separation techniques.
- the present invention does not require that all the PET is converted to BHT but rather that the polymer chain length is sufficiently shortened so that the terephthalate containing molecules are soluble in the alkanediols to permit separation of foreign materials and rapid subsequent hydrolysis.
- the short chain PET polymers and/or BHT may be purified by crystallisation in water, thereby liberating excess ethanediol.
- the precipitate is filtered off.
- the filtrate containing ethanediol is recovered using known techniques of fractional distillation from the additional water (British Patent No. 610136). Water soluble impurities such as sugar and citric acid from soft drinks may be partially removed in the filtrate and rejected as an involatile residue by distilling off the ethanediol.
- the short chain PET polymers and/or BHT are hydrolysed with water at elevated pressures and temperatures to give ethanediol and crystalline terephthalic acid.
- the hydrolysis is performed by pumping the molten BHT and water at 230 degrees Celsius into a continuous reactor held at 40 bar with a small addition of 1 % free terephthalic acid. The mixture reacts over a period of 10 minutes and is then released through a let down valve.
- the water and some ethanediol evaporate leaving a slurry of terephthalic acid crystals in ethanediol and water.
- the crystals are washed with water to remove ethanediol which is recovered as described before.
- a number of water soluble substances for example, citric acid, phosphoric acid, sodium chloride and sulphuric acid
- citric acid, phosphoric acid, sodium chloride and sulphuric acid in the feed stock will be present in the mixture of terephthalic acid and ethanediol and are separated by the filtration.
- a wide variety of compounds such as protein, paper, fats and some pesticides will be hydrolysed and made water soluble relative to the very insoluble terephthalic acid.
- the ethanediol is readily purified by distillation and may be partially recycled to give both product for further polymerisation and enough product to react with fresh PET.
- Contaminant alcohols such as methanol from ethylene methyl acrylate or hexanediol from polyester are separated by distillation. Residual alkanediols used as reactants in the method can also be separated by distillation.
- Used PET is initially subjected to transesterification with alkanediol having a temperature below the boiling point of ethanediol for a pre-determined time to embrittle PET. Additionally, a transesterification catalyst can be added to the mixture. Thereafter the mixture is passed through rollers which crush the embrittled PET.
- the non-crushed (ductile) components of the mixture are separated by screening from the remainder of the mixture.
- the PET fines are then subjected to a further transesterification process.
- Activated carbon and clay are added during transesterification to adsorb contaminants. During this further transesterification process the PET is converted into short chain PET polymers and/or BHT which are soluble.
- the resultant solution is subjected to a further separation by screening and/or high pressure filtration to remove contaminants such as activated carbon, clay, dye, PVC and glue.
- the filtrate is hydrolysed with water under elevated pressures and temperatures to form ethanediol and crystalline terephthalic acid.
- Acids for example, benzoic and citric acids
- contamination of the short chain PET polymers and/or BHT by benzoic, adipic and sebacic acid may be rectified because the free acids are approximately 1000 times more soluble in the wash water allowing some foreign polyester in the feed.
- the ethanediol and terephthalic acid are esterified to short chain PET polymers and/or BHT.
- Activated carbon and activated clay are added and then any remaining contaminants for example PVC, glue and dye are removed by filtration.
- Ethanediol 500 ml was heated to a temperature of 160 degrees Celsius. 100 grams of mixed PET and PVC was placed in the hot reagent for 80 minutes then recovered and crushed. The PET was readily crushed and the PVC was not discoloured and the original ductility was maintained.
- a solution of 2% antimony (HI) oxide in ethanediol (500 ml) was prepared and held at a temperature of 160 degrees Celsius. 100 grams of mixed PET and PVC was placed in the hot reagent for 60 minutes then recovered and crushed. The PET was readily crushed and the PVC was not discoloured and the original ductility was maintained.
- HI antimony
- a hot solution of 2% antimony (III) acetate in ethanediol (500 ml) was prepared. 100 grams of mixed PET and PVC was placed in the hot solution then recovered for the following temperatures and times: 160 degrees Celsius for 50 minutes;
- a partial solution of 5% germanium dioxide suspension in ethanediol being a saturated solution (150 ml) was prepared and held at a temperature of 160 degrees Celsius. 15 grams of mixed PET and PVC was placed in the hot solution for 60 minutes. The mixture was readily crushed and the PVC recovered without significant degradation.
- Example 4 The same partial solution of example 4 was prepared but held at a temperature of 130 degrees Celsius. 15 grams of mixed PET and PVC was placed in the hot solution for in excess of 210 minutes. The mixture was readily crushed and the PVC recovered without significant degradation .
- Example 7 100 grams of mixed PET and PVC was placed in hot 1 :6 hexanediol then recovered for the following temperatures and times:
- the crushed PET was screened using ethanediol as an aid then the fines passing the screen were heated for one hour to convert the PET to soluble products.
- a mixture of 5 grams of activated carbon and 5 grams of activated clay were added and the mixture heated and stirred for 15 minutes then filtered and the product hydrolysed to give terephthalic acid and ethanediol/water. It can be understood from the examples that the temperature required for embrittlement can be significantly reduced from that previously disclosed as necessary for adequate embrittlement. Since at these lower temperatures, the PVC was not degraded, it could be recovered in a useful state.
- the lower temperatures for transesterification in the present invention permits a more economical processing of a wider range of mixed feed stocks.
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Abstract
A process for removing contaminants from polyethylene terephthalate ('PET') components by depolymerising PET including transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET; crushing the mixture and separating uncrushed material from the crushed material which contains PET; transesterifying the crushed PET by reacting an alkanediol or alkanediols at a temperature between at or about the boiling point of ethanediol and 240 degrees Celsius with the recovered PET for a predetermined period of time to form a solution containing soluble short chain PET polymers and/or bis (hydroxy ethyl) terephthalate ester ('BHT'); recovering short chain PET polymers and/or BHT and ethanediol; and hydrolysing the recovered short chain PET polymers and/or BHT at elevated pressure and temperature for a predetermined period of time to form an ethanediol solution and crystals of terephthalic acid.
Description
IMPROVED POLYETHYLENE TEREPHTHALATE DECONTAMINATION
FIELD OF THE INVENTION
The present invention relates to a method for the decontamination of polyethylene terephthalate ("PET") components at reduced temperature. The invention also proposes a method for separating PET components from other materials.
BACKGROUND TO THE INVENTION
PET is a thermoplastic polyester that can be formed from 1:2 ethanediol and terephthalic acid by direct esterification to form bis (hydroxy ethyl) terephthalate ester ("BHT") which is then polymerised by catalysed ester exchange to useful polymers.
Traditionally, PET has been used extensively because it can be offered as an oriented film or fibre, has high tenacity, good electrical resistance and low moisture absorption together with a melting point of approximately 265 degrees Celsius.
For these reasons, its uses have been very diverse extending from being blended with cotton for wash and wear fabrics, blended with wool for worsteds and suitings, packaging films and recording tapes and containers including soft drink containers.
There are a number of applications of PET where remelting and reforming is not permissible or gives inferior properties. The reuse of PET for those applications is best achieved by degrading the polymer into the original monomers namely ethanediol and terephthalic acid then reacting the monomers together to regenerate the original PET.
In International Patent Application No. PCT/AU93/00198 a process is disclosed in which PET is made brittle by partial transesterification as a precursor to crushing and separation of the crushed material, which contains PET, from other substances. These other substances, for example, paper and poly vinyl chloride ("PVC") remain ductile, enabling the separation of non-PET substances by crushing and screening. According to the invention disclosed in the patent application, the embrittlement of PET by partial transesterification is carried out by mixing ethanediol (or alkanediols other than ethanediol) having a temperature at or about the boiling point of ethanediol with the material for a predetermined period of time. While the invention disclosed in Patent Application No. PCT/AU93/00198 represents a significant advance in the decontamination of PET-containing substances, subsequent investigations have revealed that at or about the atmospheric boiling point of ethanediol, the non-PET substances, such as paper and PVC, may be adversely affected. PVC, in particular, may be chemically degraded in such a way as to alter its ability to be
commercially recovered. For example, at or about the boiling point of ethanediol PVC is severely degraded as it is dehydrochlorinated which yields a brown brittle product. The resultant brown product is not suitable for re-extrusion to make commercially useful recycled products. Consequently, further investigation have been directed towards the process of PET decontamination with the view of balancing the need for adequate embrittlement of PET whilst avoiding unwanted degradation of non-PET components.
SUMMARY OF THE INVENTION
Surprisingly it has now been found that satisfactory levels of embrittlement of PET components can be achieved at temperatures below the boiling point of ethanediol. As non- PET components are less susceptible to degradation at these lower temperatures, it is now possible to partially transesterify PET without adversely affecting those other components.
Thus, according to the present invention, a process is provided for removing contaminants from PET components by depolymerising PET, including the following steps: (a) transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET;
(b) crushing the mixture and separating uncrushed material from the crushed material which contains PET; (c) transesterifying the crushed PET by reacting an alkanediol or alkanediols at a temperature between at or about the boiling point of ethanediol and 240 degrees Celsius with the recovered PET for a predetermined period of time to form a solution containing soluble short chain PET polymers and/or BHT;
(d) recovering short chain PET polymers and/or BHT and ethanediol; and (e) hydrolysing the recovered short chain PET polymers and/or BHT at elevated pressure and temperature for a predetermined period of time to form an ethanediol solution and crystals of terephthalic acid.
The invention further provides a process for removing contaminants from PET components by depolymerising PET, including the following steps: (a) transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET;
(b) crushing the mixture and separating uncrushed material from the crushed material which contains PET;
(c) hydrolysing the crushed PET at elevated pressure and temperature for a predetermined period of time to form an ethanediol solution and crystals of terephthalic acid;
(d) esterifying the ethanediol solution and crystals of terephthalic acid to form short chain PET polymers and/or BHT; and
(e) recovering short chain PET polymers and/or BHT from the mixture.
The invention further provides a process for separating PET components from other materials, including the following steps:
(a) transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET; and
(b) crushing the mixture and separating uncrushed material from the crushed material which contains PET.
In preferred forms of the invention, the alkanediol or alkanediols are selected from the group including ethanediol, 1:4 butanediol and 1:6 hexanediol and mixtures thereof. Ethanediol is particularly preferable as it is one of the monomers used in the direct esterification to form PET. The use of alkanediols other than ethanediol therefore introduces into the reaction a substance which must ultimately be separated.
The temperature of the alkanediol or alkanediols used in steps (a) above in the transesterification of the PET component is preferably in the range of 130 degrees Celsius to within 10 degrees Celsius of the boiling point of ethanediol and is particularly preferred to be in the range of 140 degrees Celsius to 160 degrees Celsius. This latter temperature range is preferred when separation of PVC or other non-PET components is desired for re¬ use. This will significantly avoid degradation of PVC by dehydrochlorination which poses problems with the re-use of PVC. The release of hydrogen chloride in the reactor is also substantially eliminated.
The predetermined time for embrittlement may commercially lie in the range of up to 150 minutes although, of course, longer times may still achieve the desired level of embrittlement of PET without adverse effect upon contaminants. In a preferred form of the invention, embrittlement is caused to occur within a period of between 30 minutes and 120 minutes and more preferably, between 45 minutes and 60 minutes. The transesterification giving embrittlement is preferably controlled by both temperature and time to give a brittle product with minimum over treatment. This can be effected by using plug flow reactors with a narrow range of residence times. However, if the residence time is not critical to the cost of the process then there is no technical limitation on residence time. It is anticipated
that most process designers will select a residence time between 45 and 60 minutes to enable the use of a smaller sized plant. The use of a time of more than 45 minutes also substantially ensures only a small range in the residence times, so giving a small range in the degree of brittleness of PET. It is known that the production of PET from BHT can be improved by using a wide range of transesterification catalysts. For example, United States Patent No. 2 534 028, United States Patent No. 2 518 283, United States Patent No. 2 641 592, United States Patent No. 2 578 660, United States Patent No. 2 643 989, United States Patent No. 2 662 093, United States Patent No. 2 647 885 and United States Patent No. 2 491 660 describe methods for using suitable catalysts. Typically it is common to employ antimony (HI) oxide, antimony (HI) acetate and germanium dioxide as the catalyst in the esterification of PET.
Surprisingly, it has also been found that the addition of transesterification catalysts to the alkanediol or alkanediols further reduces the temperature or time necessary to achieve the required embrittlement. This is particularly useful if the time for embrittlement is uneconomical and the addition of catalyst can reduce the time to an economic residence time. Alternatively, the reduced reaction temperature can be valuable if a reduced vapour pressure of ethanediol is to be used, or temperatures which degrade other useful substances mixed with PET are to be avoided. The addition of catalyst to the mixture for transesterification, supplements the small pre-existing concentration of catalyst in the feed stock PET, residual from the original polymerisation.
Preferably, the transesterification catalyst may be the known useful transesterification catalysts selected from the group including antimony (HI) oxide, antimony (HI) acetate, germanium dioxide, manganese acetate, terra butoxy titanium and mixtures thereof. Those skilled in the art would understand that any of the known transesterification catalysts would have a similar action, but may be less acceptable to consumers as coloured by¬ products are generated by the other disclosed catalysts.
Embrittlement, which takes place prior to the collapse of the original PET structure allows the PET to be crushed to separate it from the contaminants. This allows separation to take place on the basis of size and density. Crushing to a diameter of less than 1 millimetre is preferred. Crushing can be achieved by rollers or hammer mills or any other known techniques for reducing the size of particles. Once crushed, the PET is separated from typical contaminants such as hydrocarbons and pigments from paper. Other substances giving rise to coloured products can be separated by screening, washing or density separation from other contaminants which have not become embrittled. A number of substances such as Nylons dissolve in the hot alkanediols and are removed with the liquid alkanediol. Preferably, the uncrushed material includes PVC.
Preferably, the temperature of the alkanediol or alkanediols in the transesterification of the crushed PET which form a solution of short chain PET polymers and BHT, is within the range of between at or about the boiling point of ethanediol (preferably within 5 or 10 degrees Celsius of the boiling point of ethanediol) and 240 degrees Celsius. In a particularly preferred form of the invention, the temperature range is between 220 degrees Celsius and 240 degrees Celsius. Again, preferably the alkanediols are selected from the group including ethanediol, 1:4 butanediol and 1:6 hexanediol and mixtures thereof. Ethanediol is most preferred.
Once solubilised, separation of the PET rich fraction in one preferred form of the invention can take place by filtration methods and more preferably by high pressure filtration methods. The addition of activated carbon or a combination of activated carbon and activated clay is used as an adsorbent for a wide variety of molecules such as dyes, pesticides, coloured polymers, etc. If alkanediols other than ethanediol have been used, they can also be removed at this time by known separation techniques. Other foreign plastics with an alkane chain do not depolymeri.se in the alkanediol but only melt so that they may be removed by either flotation on the denser alkanediol (for example, ethanediol 1114 kilograms/m3) or screened from embrittled PET or the short chain PET polymer and/or BHT solution. Proteins and polyamides that do not react with alkanediol are recovered with the other plastics. Other polyesters are also transesterified and contaminate the short chain PET polymer solution.
It is to be understood that the present invention does not require that all the PET is converted to BHT but rather that the polymer chain length is sufficiently shortened so that the terephthalate containing molecules are soluble in the alkanediols to permit separation of foreign materials and rapid subsequent hydrolysis. Following transesterification, the short chain PET polymers and/or BHT may be purified by crystallisation in water, thereby liberating excess ethanediol. The precipitate is filtered off. The filtrate containing ethanediol is recovered using known techniques of fractional distillation from the additional water (British Patent No. 610136). Water soluble impurities such as sugar and citric acid from soft drinks may be partially removed in the filtrate and rejected as an involatile residue by distilling off the ethanediol.
The short chain PET polymers and/or BHT are hydrolysed with water at elevated pressures and temperatures to give ethanediol and crystalline terephthalic acid. Typically the hydrolysis is performed by pumping the molten BHT and water at 230 degrees Celsius into a continuous reactor held at 40 bar with a small addition of 1 % free terephthalic acid. The mixture reacts over a period of 10 minutes and is then released through a let down valve. The water and some ethanediol evaporate leaving a slurry of terephthalic acid crystals in
ethanediol and water. The crystals are washed with water to remove ethanediol which is recovered as described before.
A number of water soluble substances (for example, citric acid, phosphoric acid, sodium chloride and sulphuric acid) in the feed stock will be present in the mixture of terephthalic acid and ethanediol and are separated by the filtration. Additionally, a wide variety of compounds such as protein, paper, fats and some pesticides will be hydrolysed and made water soluble relative to the very insoluble terephthalic acid.
The ethanediol is readily purified by distillation and may be partially recycled to give both product for further polymerisation and enough product to react with fresh PET. Contaminant alcohols such as methanol from ethylene methyl acrylate or hexanediol from polyester are separated by distillation. Residual alkanediols used as reactants in the method can also be separated by distillation.
Where in this specification reference is made to the boiling point of ethanediol, it is taken to be 196-197 degrees Celsius. DESCRIPTION OF THE DIAGRAM
One form of the invention is illustrated in the accompanying flow chart.
Used PET is initially subjected to transesterification with alkanediol having a temperature below the boiling point of ethanediol for a pre-determined time to embrittle PET. Additionally, a transesterification catalyst can be added to the mixture. Thereafter the mixture is passed through rollers which crush the embrittled PET.
The non-crushed (ductile) components of the mixture are separated by screening from the remainder of the mixture. The PET fines are then subjected to a further transesterification process.
Activated carbon and clay are added during transesterification to adsorb contaminants. During this further transesterification process the PET is converted into short chain PET polymers and/or BHT which are soluble.
The resultant solution is subjected to a further separation by screening and/or high pressure filtration to remove contaminants such as activated carbon, clay, dye, PVC and glue.
The filtrate is hydrolysed with water under elevated pressures and temperatures to form ethanediol and crystalline terephthalic acid. Acids (for example, benzoic and citric acids) remain in solution and are separated from crystalline terephthalic acid. It will be understood by persons skilled in that art that contamination of the short chain PET polymers and/or BHT by benzoic, adipic and sebacic acid may be rectified because the free
acids are approximately 1000 times more soluble in the wash water allowing some foreign polyester in the feed.
The ethanediol and terephthalic acid are esterified to short chain PET polymers and/or BHT. Activated carbon and activated clay are added and then any remaining contaminants for example PVC, glue and dye are removed by filtration.
EXAMPLES
The invention will now be further illustrated by the following non-limiting examples.
The examples were all carried out at atmospheric pressure. It should be understood by those skilled in the art that the pressure should be reduced until a reaction temperature is reached to allow control of water in the reaction mixture.
Example 1
Ethanediol (500 ml) was heated to a temperature of 160 degrees Celsius. 100 grams of mixed PET and PVC was placed in the hot reagent for 80 minutes then recovered and crushed. The PET was readily crushed and the PVC was not discoloured and the original ductility was maintained.
Example 2
A solution of 2% antimony (HI) oxide in ethanediol (500 ml) was prepared and held at a temperature of 160 degrees Celsius. 100 grams of mixed PET and PVC was placed in the hot reagent for 60 minutes then recovered and crushed. The PET was readily crushed and the PVC was not discoloured and the original ductility was maintained.
Example 3
A hot solution of 2% antimony (III) acetate in ethanediol (500 ml) was prepared. 100 grams of mixed PET and PVC was placed in the hot solution then recovered for the following temperatures and times: 160 degrees Celsius for 50 minutes;
150 degrees Celsius for 60 minutes; and
140 degrees Celsius for 120 minutes.
In each test, the PET was readily crushed and the PVC was not discoloured and the original ductility was maintained.
Example 4
A partial solution of 5% germanium dioxide suspension in ethanediol being a saturated solution (150 ml) was prepared and held at a temperature of 160 degrees Celsius. 15 grams of mixed PET and PVC was placed in the hot solution for 60 minutes. The mixture was readily crushed and the PVC recovered without significant degradation.
Example 5
The same partial solution of example 4 was prepared but held at a temperature of 130 degrees Celsius. 15 grams of mixed PET and PVC was placed in the hot solution for in excess of 210 minutes. The mixture was readily crushed and the PVC recovered without significant degradation .
Example 6
100 grams of mixed PET and PVC was placed in hot 1 :4 butanediol then recovered for the following temperatures and times:
190 degrees Celsius for 50 minutes; 170 degrees Celsius for 120 minutes; and
155 degrees Celsius for 180 minutes.
In each test, the PET was readily crushed. In this example at 170 degrees Celcius and 155 degrees Celsius, the PVC was not discoloured and the original ductility was maintained.
Example 7 100 grams of mixed PET and PVC was placed in hot 1 :6 hexanediol then recovered for the following temperatures and times:
190 degrees Celsius for 50 minutes;
170 degrees Celsius for 120 minutes; and
155 degrees Celsius for 180 minutes. In each test, the PET was readily crushed. In this example at 170 degrees Celsius and 155 degrees Celsius, the PVC was not discoloured and the original ductility was maintained.
In all of the above examples, the crushed PET was screened using ethanediol as an aid then the fines passing the screen were heated for one hour to convert the PET to soluble products. A mixture of 5 grams of activated carbon and 5 grams of activated clay were added and the mixture heated and stirred for 15 minutes then filtered and the product hydrolysed to give terephthalic acid and ethanediol/water.
It can be understood from the examples that the temperature required for embrittlement can be significantly reduced from that previously disclosed as necessary for adequate embrittlement. Since at these lower temperatures, the PVC was not degraded, it could be recovered in a useful state.
Accordingly, the lower temperatures for transesterification in the present invention permits a more economical processing of a wider range of mixed feed stocks.
Since modifications to the steps described are various and obvious to those skilled in the art, it is to be understood that this invention is not limited to the particular embodiments described.
Claims
1. A process for removing contaminants from polyethylene terephthalate ("PET") components by depolymerising PET, including the following steps:
(a) transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET;
(b) crushing the mixture and separating uncrushed material from the crushed material which contains PET; (c) transesterifying the crushed PET by reacting an alkanediol or alkanediols at a temperature between at or about the boiling point of ethanediol and 240 degrees Celsius with the recovered PET for a predetermined period of time to form a solution containing soluble short chain PET polymers and/or bis (hydroxy ethyl) terephthalate ester ("BHT"); (d) recovering short chain PET polymers and/or BHT and ethanediol; and
(e) hydrolysing the recovered short chain PET polymers and/or BHT at elevated pressure and temperature for a predetermined period of time to form an ethanediol solution and crystals of terephthalic acid.
2. The process of claim 1, wherein the alkanediol or alkanediols are selected from the group including ethanediol, 1:4 butanediol and 1:6 hexanediol and mixtures thereof.
3. The process of claim 1, wherein the alkanediol is ethanediol.
4. The process of any one of claims 1 to 3, wherein step (a) is carried out at a temperature in the range of between 130 degrees Celsius and within 10 degrees Celsius of the boiling point of ethanediol.
5. The process of any one of claims 1 to 3, wherein step (a) is carried out at a temperature in the range of between 140 degrees Celsius and 160 degrees Celsius.
6. The process of any one of claims 1 to 5, wherein the uncrushed material includes poly vinyl chloride.
7. The process of any one of claims 1 to 6, wherein the predetermined period of time in step (a) is between 30 minutes and 120 minutes.
8. The process of any one of claims 1 to 6, wherein the predetermined period of time in step (a) is between 45 minutes and 60 minutes.
9. The process of any one of claims 1 to 8, wherein step (a) further includes the addition of a transesterification catalyst.
10. The process of claim 9, wherein the transesterification catalyst is selected from the group including antimony (HI) oxide, antimony (HI) acetate, germanium dioxide, manganese acetate, tetra butoxy titanium oand mixtures thereof.
11. The process of any one of claims 1 to 10, wherein the PET is crushed to a size of less than 1 millimetre.
12. The process of any one of claims 1 to 11, wherein in step (c) the range is between a temperature within 10 degrees Celsius of the boiling point of ethanediol and 240 degrees Celsius.
13. The process of any one of claims 1 to 11, wherein in step (c) the range is between a temperature within 5 degrees Celsius of the boiling point of ethanediol and 240 degrees Celsius.
14. The process of any one of claims 1 to 11, wherein step (c) is carried out at a temperature of between 220 degrees Celsius and 240 degrees Celsius.
15. The process of any one of claims 1 to 14, wherein the PET polymers and/or BHT and ethanediol are recovered in step (d) by filtration.
16. The process of claim 15, wherein the filtration is high pressure filtration.
17. The process according to claim 16, wherein the filtration includes the addition of activated carbon or a combination of activated carbon and activated clay.
18. A process for removing contaminants from polyethylene terephthalate ("PET") components by depolymerising PET, including the following steps:
(a) transesterifying the material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET;
(b) crushing the mixture and separating uncrushed material from the crushed material which contains PET;
(c) hydrolysing the crushed PET at elevated pressure and temperature for a predetermined period of time to form an ethanediol solution and crystals of terephthalic acid; (d) esterifying the ethanediol solution and crystals of terephthalic acid to form short chain PET polymers and/or bis (hydroxy ethyl) terephthalate ester ("BHT"); and
(e) recovering short chain PET polymers and/or BHT from the mixture.
19. The process of claim 18, wherein the alkanediol or alkanediols are selected from the group including ethanediol, 1:4 butanediol and 1:6 hexanediol and mixtures thereof.
20. The process of claim 18, wherein the alkanediol is ethanediol.
21. The process of any one of claims 18 to 21, wherein step (a) is carried out at a temperature in the range of 130 degrees Celsius and within 10 degrees of the boiling point of ethanediol .
22. The process of any one of claims 18 to 21, wherein step (a) is carried out at a temperature in the range of between 140 degrees Celsius and 160 degrees Celsius.
23. The process of any one of claims 18 to 22, wherein the uncrushed material includes poly vinyl chloride.
24. The process of any one of claims 18 to 23, wherein the predetermined period of time in step (a) is between 30 minutes and 120 minutes.
25. The process of any one of claims 18 to 23, wherein the predetermined period of time in step (a) is between 45 minutes and 60 minutes.
26. The process of any one of claims 18 to 25, wherein step (a) further includes the addition of a transesterification catalyst.
27. The process of claim 27, wherein the transesterification catalyst is selected from the group including antimony (III) oxide, antimony (HI) acetate, germanium dioxide, manganese acetate, tetra butoxy titanium and mixtures thereof.
28. The process of any one of claims 18 to 27, wherein the PET is crushed to a size of less than 1 millimetre.
29. The process of any one of claims 18 to 28, wherein the PET polymers and/or BHT are recovered in step (e) by filtration.
30. The process of claim 29, wherein the filtration is high pressure filtration.
31. The process according to claim 30, wherein the filtration includes the addition of activated carbon or a combination of activated carbon and activated clay.
32. A process for recycling polyethylene terephthalate ("PET") from sources of used PET, including the steps of any one of claims 1 to 31.
33. Short chain PET polymers and/or BHT when recovered according to the process of any one of claims 18 to 31.
34. A process for separating polyethylene terephthalate ("PET") components from other materials, including the following steps: (a) transesterifying material containing PET by reacting an alkanediol or alkanediols at a temperature below the boiling point of ethanediol with the material for a predetermined period of time to form a mixture containing embrittled PET; and
(b) crushing the mixture and separating uncrushed material from the crushed material which contains PET.
35. The process of claim 34, wherein the alkanediol or alkanediols are selected from the group including ethanediol, 1:4 butanediol and 1:6 hexanediol and mixtures thereof.
36. The process of claim 34, wherein the alkanediol is ethanediol.
37. The process of any one of claims 34 to 37, wherein step (a) is carried out at a temperature in the range of between 130 degrees Celsius and within 10 degrees Celsius of the boiling point of ethanediol.
38. The process of any one of claims 34 to 37, wherein step (a) is carried out at a temperature in the range of between 140 degrees Celsius and 160 degrees Celsius.
39. The process of any one of claims 34 to 38, wherein the uncrushed material includes poly vinyl chloride.
40. The process of any one of claims 34 to 39, wherein the predetermined period of time in step (a) is between 30 minutes and 120 minutes.
41. The process of any one of claims 34 to 39, wherein the predetermined period of time in step (a) is between 45 minutes and 60 minutes.
42. The process of any one of claims 34 to 41, wherein step (a) further includes the addition of a transesterification catalyst.
43. The process of claim 42, wherein the transesterification catalyst is selected from the group including antimony (III) oxide, antimony (III) acetate, germanium dioxide, manganese acetate, tetra butoxy titanium and mixtures thereof.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AU21331/95A AU2133195A (en) | 1994-04-11 | 1995-04-11 | Improved polyethylene terephthalate decontamination |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AUPM4993A AUPM499394A0 (en) | 1994-04-11 | 1994-04-11 | Improved polyethylene terephthalate decontamination |
| AUPM4993 | 1994-04-11 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO1995027753A1 true WO1995027753A1 (en) | 1995-10-19 |
Family
ID=3779573
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/AU1995/000201 Ceased WO1995027753A1 (en) | 1994-04-11 | 1995-04-11 | Improved polyethylene terephthalate decontamination |
Country Status (5)
| Country | Link |
|---|---|
| AU (1) | AUPM499394A0 (en) |
| MY (1) | MY128311A (en) |
| TW (1) | TW345587B (en) |
| WO (1) | WO1995027753A1 (en) |
| ZA (1) | ZA952933B (en) |
Cited By (18)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2000047658A1 (en) * | 1999-02-10 | 2000-08-17 | Eastman Chemical Company | Process for recycling polyesters |
| EP1134211A1 (en) * | 2000-02-29 | 2001-09-19 | Massimo Broccatelli | Method of recovering chemical species by depolymerization of poly(ethylene terephthalate) and related use |
| EP1138663A1 (en) * | 2000-02-29 | 2001-10-04 | Massimo Broccatelli | Method for recovery of terephthalic acid from a material containing poly(ethylene terephthalates) |
| WO2001068581A3 (en) * | 2000-03-17 | 2002-04-04 | Milan Sirek | The method of chemical recycling of polyethylene terephthalate waste |
| US6720448B2 (en) | 2000-10-11 | 2004-04-13 | Massimo Broccatelli | Method of recovering chemical species by depolymerization of poly (ethylene terephthalate) and related use |
| WO2005079140A3 (en) * | 2003-02-27 | 2006-05-04 | Petrecycle Ltd | A method for the decontamination of polyethylene terephthalate |
| US8889820B2 (en) | 2012-02-15 | 2014-11-18 | Saudi Basic Industries Corporation | Amorphous, high glass transition temperature copolyester compositions, methods of manufacture, and articles thereof |
| US8895660B2 (en) | 2012-03-01 | 2014-11-25 | Saudi Basic Industries Corporation | Poly(butylene-co-adipate terephthalate), method of manufacture, and uses thereof |
| US8901273B2 (en) | 2012-02-15 | 2014-12-02 | Saudi Basic Industries Corporation | Amorphous, high glass transition temperature copolyester compositions, methods of manufacture, and articles thereof |
| US9234074B2 (en) | 2012-04-20 | 2016-01-12 | Perpetual Global Technologies Limited | Flakes of ester mixtures and methods for their production |
| US9550713B1 (en) | 2015-07-09 | 2017-01-24 | Loop Industries, Inc. | Polyethylene terephthalate depolymerization |
| US9828461B2 (en) | 2012-03-01 | 2017-11-28 | Sabic Global Technologies B.V. | Poly(alkylene co-adipate terephthalate) prepared from recycled polyethylene terephthalate having low impurity levels |
| US10252976B1 (en) | 2017-09-15 | 2019-04-09 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US10808096B2 (en) | 2018-06-25 | 2020-10-20 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| CN112708947A (en) * | 2020-12-14 | 2021-04-27 | 浙江理工大学 | Preparation method of self-crimping fiber with recycled polyester as raw material |
| US11248103B2 (en) | 2019-03-20 | 2022-02-15 | 9449710 Canada Inc. | Process for the depolymerization of polyethylene terephthalate (PET) |
| CN116554025A (en) * | 2023-05-19 | 2023-08-08 | 广东绿王新材料有限公司 | A method for chemically preparing BHET powder from polyester bottle flakes |
| US12071519B2 (en) | 2017-09-15 | 2024-08-27 | 9449710 Canada Inc. | Terephthalic acid esters formation |
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| US3776945A (en) * | 1970-11-26 | 1973-12-04 | Sir Soc Italiana Resine Spa | Method of depolymerizing poly-ethylene terephthalate |
| GB2123403A (en) * | 1982-07-09 | 1984-02-01 | Celanese Mexicana Sa | Continuous procedure for obtaining pure terephthalic acid and glycol starting from polyethylene terephthalate waste |
| US5298530A (en) * | 1992-11-25 | 1994-03-29 | Eastman Kodak Company | Process of recovering components from scrap polyester |
-
1994
- 1994-04-11 AU AUPM4993A patent/AUPM499394A0/en not_active Abandoned
-
1995
- 1995-04-08 MY MYPI9500915 patent/MY128311A/en unknown
- 1995-04-10 TW TW082103797A01A patent/TW345587B/en active
- 1995-04-10 ZA ZA952933A patent/ZA952933B/en unknown
- 1995-04-11 WO PCT/AU1995/000201 patent/WO1995027753A1/en not_active Ceased
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3776945A (en) * | 1970-11-26 | 1973-12-04 | Sir Soc Italiana Resine Spa | Method of depolymerizing poly-ethylene terephthalate |
| GB2123403A (en) * | 1982-07-09 | 1984-02-01 | Celanese Mexicana Sa | Continuous procedure for obtaining pure terephthalic acid and glycol starting from polyethylene terephthalate waste |
| US5298530A (en) * | 1992-11-25 | 1994-03-29 | Eastman Kodak Company | Process of recovering components from scrap polyester |
Cited By (31)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2000047658A1 (en) * | 1999-02-10 | 2000-08-17 | Eastman Chemical Company | Process for recycling polyesters |
| US6472557B1 (en) | 1999-02-10 | 2002-10-29 | Eastman Chemical Company | Process for recycling polyesters |
| US6670503B2 (en) | 2000-02-29 | 2003-12-30 | Massimo Broccatelli | Method for recovery of terephthalic acid from a material containing poly(ethylene terephthalates) |
| EP1134211A1 (en) * | 2000-02-29 | 2001-09-19 | Massimo Broccatelli | Method of recovering chemical species by depolymerization of poly(ethylene terephthalate) and related use |
| EP1138663A1 (en) * | 2000-02-29 | 2001-10-04 | Massimo Broccatelli | Method for recovery of terephthalic acid from a material containing poly(ethylene terephthalates) |
| WO2001068581A3 (en) * | 2000-03-17 | 2002-04-04 | Milan Sirek | The method of chemical recycling of polyethylene terephthalate waste |
| US6649792B2 (en) | 2000-03-17 | 2003-11-18 | Sirek Milan | Method of chemical recycling of polyethylene terephthalate waste |
| KR100693707B1 (en) * | 2000-03-17 | 2007-03-13 | 밀란 시렉 | Chemical recycling method of polyethylene terephthalate waste |
| US6720448B2 (en) | 2000-10-11 | 2004-04-13 | Massimo Broccatelli | Method of recovering chemical species by depolymerization of poly (ethylene terephthalate) and related use |
| WO2005079140A3 (en) * | 2003-02-27 | 2006-05-04 | Petrecycle Ltd | A method for the decontamination of polyethylene terephthalate |
| US7214723B2 (en) | 2003-02-27 | 2007-05-08 | Petrecycle Ltd. | Method for the decontamination of polyethylene terephthalate |
| US8889820B2 (en) | 2012-02-15 | 2014-11-18 | Saudi Basic Industries Corporation | Amorphous, high glass transition temperature copolyester compositions, methods of manufacture, and articles thereof |
| US8901273B2 (en) | 2012-02-15 | 2014-12-02 | Saudi Basic Industries Corporation | Amorphous, high glass transition temperature copolyester compositions, methods of manufacture, and articles thereof |
| US8895660B2 (en) | 2012-03-01 | 2014-11-25 | Saudi Basic Industries Corporation | Poly(butylene-co-adipate terephthalate), method of manufacture, and uses thereof |
| US9828461B2 (en) | 2012-03-01 | 2017-11-28 | Sabic Global Technologies B.V. | Poly(alkylene co-adipate terephthalate) prepared from recycled polyethylene terephthalate having low impurity levels |
| US9234074B2 (en) | 2012-04-20 | 2016-01-12 | Perpetual Global Technologies Limited | Flakes of ester mixtures and methods for their production |
| US9550713B1 (en) | 2015-07-09 | 2017-01-24 | Loop Industries, Inc. | Polyethylene terephthalate depolymerization |
| US10087130B2 (en) | 2015-07-09 | 2018-10-02 | Loop Industries, Inc. | Polyethylene terephthalate depolymerization |
| US10640442B2 (en) | 2015-07-09 | 2020-05-05 | Loop Industries, Inc. | Polyethylene terephthalate depolymerization |
| US10252976B1 (en) | 2017-09-15 | 2019-04-09 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US10793508B2 (en) | 2017-09-15 | 2020-10-06 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US12071519B2 (en) | 2017-09-15 | 2024-08-27 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US11866404B2 (en) | 2017-09-15 | 2024-01-09 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US10808096B2 (en) | 2018-06-25 | 2020-10-20 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US11401398B2 (en) | 2018-06-25 | 2022-08-02 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US12071520B2 (en) | 2018-06-25 | 2024-08-27 | 9449710 Canada Inc. | Terephthalic acid esters formation |
| US11248103B2 (en) | 2019-03-20 | 2022-02-15 | 9449710 Canada Inc. | Process for the depolymerization of polyethylene terephthalate (PET) |
| US12415901B2 (en) | 2019-03-20 | 2025-09-16 | 9449710 Canada Inc. | Process for the depolymerization of polyethylene terephthalate (PET) |
| US11795291B2 (en) | 2019-03-20 | 2023-10-24 | 9449710 Canada Inc. | Process for the depolymerization of polyethylene terephthalate (PET) |
| CN112708947A (en) * | 2020-12-14 | 2021-04-27 | 浙江理工大学 | Preparation method of self-crimping fiber with recycled polyester as raw material |
| CN116554025A (en) * | 2023-05-19 | 2023-08-08 | 广东绿王新材料有限公司 | A method for chemically preparing BHET powder from polyester bottle flakes |
Also Published As
| Publication number | Publication date |
|---|---|
| TW345587B (en) | 1998-11-21 |
| AUPM499394A0 (en) | 1994-05-05 |
| ZA952933B (en) | 1996-11-05 |
| MY128311A (en) | 2007-01-31 |
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