CN101250285A - Method for degrading bis-hydroxyethyl terephthalate - Google Patents
Method for degrading bis-hydroxyethyl terephthalate Download PDFInfo
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- CN101250285A CN101250285A CNA2007101757042A CN200710175704A CN101250285A CN 101250285 A CN101250285 A CN 101250285A CN A2007101757042 A CNA2007101757042 A CN A2007101757042A CN 200710175704 A CN200710175704 A CN 200710175704A CN 101250285 A CN101250285 A CN 101250285A
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- Prior art keywords
- polyethylene terephthalate
- degrading
- pet
- coo
- charged ion
- Prior art date
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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
Abstract
The invention relates to a process for degrading polyethylene glycol terephthalate (PET) through utilizing ion liquid, which is characterized in that degrading polyethylene glycol terephthalate with ion liquid, and reacting under the condition of no adding any catalyst. The process degrades PET polyester through utilizing ion liquid which has the solvent function, and has the advantages of difficult volatilization of ion liquid, environment-friendly and mild reaction conditions and the like.
Description
Technical field:
The present invention relates to a kind of ionic liquid that utilizes, do not use the method for catalyst degradation polyethylene terephthalate.
Background technology:
Polyethylene terephthalate (PET) is a kind of thermoplastic macromolecule material of excellent property, because of it has good physical and chemical performance, be widely used in fields such as food product pack, beverage, film, medicine, sensitive film, finishing material, electrically insulating material, fiber, sheet base.Along with the swift and violent increase of polyester material volume of production and marketing, the amount of the waste and old polyester material that is produced will get more and more.2004, China PET polyester yearly capacity was about 6,000,000 tons, and its consumption is still increasing with the speed in every year 11%, wherein has every year millions of tons of polyester to become waste material approximately.Though the toxicity of these polyester waste materials own is little, because its light weight, bulky, and is difficult under the natural condition and degrades, thereby not only can cause very big influence, and can cause the huge wasting of resources environment.As the important channel of turning waste into wealth and solving ecological environmental pollution, the recovery and utilization technology of waste and old polyester more and more is subjected to the attention of countries in the world.
Traditional chemical recovery PET polyester is produced monomer and is mainly contained following several method: methyl alcohol alcoholysis, glycolysis and hydrolysis.Though adopting chemical recovery method can be monomer or industrial chemicals with the PET polyester depolymerization of giving up, realize the recycle of PET polyester waste material, still there are many unfavorable factors in aforesaid method, as: the organic solvent of using in the degradation process is volatile, contaminate environment; Severe reaction conditions needs High Temperature High Pressure usually; The glycolysis product is complicated, and many oligomers are wherein arranged; Acid-base solution meeting etching apparatus in the hydrolytic process, contaminate environment.So the present invention is a purpose with the depolymerizing agent environmentally friendly, that reaction conditions is gentle of exploitation degraded PET polyester.
Summary of the invention:
Research and utilization ionic liquid of the present invention, degraded PET polyester under the reaction conditions that does not add any catalyzer, gentleness.
The molecular weight of used polyethylene terephthalate is 6.2~6.8 * 10
4G/mol.
Used ion liquid positively charged ion is selected from a kind of in glyoxaline cation (1), pyridylium (2), season phosphine positively charged ion (3), the quaternary ammonium cation (4), and structure is as follows:
Negatively charged ion is selected from Cl
-, Br
-, I
-, AlCl
4 -, AlBr
4 -, AlI
4 -, CF
3COO
-, CH
3COO
-, CF
3SO
3 -, SCN
-, (CF
3SO
2)
2N
-, (CF
3SO
2)
3C
-, o-C
6H
4(OH) (COO
-) in a kind of.Wherein, the substituting group on (1), (2), (3) and (4) is selected from a kind of in alkane, halohydrocarbon, hydroxyl, aromatic hydrocarbons, the heterocycle hydro carbons, can be identical, also can be different, and the carbon number of aliphatic chain organic substituent group is between 1~14.
Because ionic liquid has good solubility, and volatilization hardly, so this method has reaction conditions gentleness, advantages of environment protection.
The temperature of reaction of ionic liquid degraded polyethylene terephthalate is 50 ℃ to 250 ℃, preferred 120 ℃ to 200 ℃.
Ionic liquid degraded polyethylene terephthalate does not have particular requirement to reaction pressure.
The time of ionic liquid degraded polyethylene terephthalate is 6 hours to 24 hours.
Embodiment:
The present invention illustrates with following embodiment, but the invention is not restricted to following embodiment, under the scope of described aim, changes and implements to be included in the technical scope of the present invention before and after not breaking away from.
Embodiment 1
Implementation method: in the 50ml there-necked flask, add 5.0gPET particle, 20.0g1-butyl-3-Methylimidazole villaumite ([bmim] Cl) successively.Control reaction temperature is 180 ℃, and pressure is 1atm, and 8 hours postcooling of condensing reflux reaction are isolated undegradable PET particle to room temperature, thorough washing, drying, weigh the quality of the PET that do not degrade.Draw with this understanding, the degradation rate of PET polyester is 49.54%.
Embodiment 2
Implementation method: in the 50ml there-necked flask, add 5.0gPET particle, 20.0g1-butyl-3-Methylimidazole bromine salt ([bmim] Br) successively.Control reaction temperature is 180 ℃, and pressure is 1atm, and 8 hours postcooling of condensing reflux reaction are isolated undegradable PET particle to room temperature, thorough washing, drying, weigh the quality of undegradable PET.Draw with this understanding, the degradation rate of PET polyester is 6.96%.
Embodiment 3
Implementation method: in the 50ml there-necked flask, add 5.0gPET particle, 20.0g1-ethyl-3-Methylimidazole bromine salt ([emim] Br) successively.Control reaction temperature is 180 ℃, and pressure is 1atm, and 8 hours postcooling of condensing reflux reaction are isolated undegradable PET particle to room temperature, thorough washing, drying, weigh the quality of undegradable PET.Draw with this understanding, the degradation rate of PET polyester is 2.90%.
Embodiment 4
Implementation method: in the 50ml there-necked flask, add 5.0gPET particle, 20.0g1-butyl-3-Methylimidazole trifluoroacetate ([bmim] CF successively
3COO).Control reaction temperature is 120 ℃, and pressure is 1atm, and 8 hours postcooling of condensing reflux reaction are isolated undegradable PET particle to room temperature, thorough washing, drying, weigh the quality of undegradable PET.Draw with this understanding, the degradation rate of PET polyester is 7.63%.
Embodiment 5
Implementation method: in the 50ml there-necked flask, add 5.0gPET particle, 20.0g1-butyl-3-Methylimidazole chloro-aluminate ([bmim] AlCl successively
4).Control reaction temperature is 150 ℃, and pressure is 1atm, and 8 hours postcooling of condensing reflux reaction are isolated undegradable PET particle to room temperature, thorough washing, drying, weigh the quality of undegradable PET.Draw with this understanding, the degradation rate of PET polyester is 29.90%.
Embodiment 6
Implementation method: in the 50ml there-necked flask, add 5.0gPET particle, 20.0g β hydroxyethyl trimethyl ammonium salicylic acid salt ([N successively
+ 111(CH
2)
2OH] C
6H
4(OH) (COO)).Control reaction temperature is 180 ℃, and pressure is 1atm, and 8 hours postcooling of condensing reflux reaction are isolated undegradable PET particle to room temperature, thorough washing, drying, weigh the quality of undegradable PET.Draw with this understanding, the degradation rate of PET polyester is 53.80%.
Embodiment 7
With embodiment 1, control reaction temperature is 200 ℃, and then the degradation rate of PET polyester is 64.58% 200 ℃ the time.
Claims (6)
1. the method for the polyethylene terephthalate of degrading is characterized in that with the ionic liquid being depolymerizing agent, descends in the condition that does not add any catalyzer and separates polyethylene terephthalate.
2. method according to claim 1, the molecular weight that it is characterized in that used polyethylene terephthalate is 6.2~6.8 * 10
4G/mol.
3. method according to claim 1, used ion liquid positively charged ion are selected from a kind of in glyoxaline cation (1), pyridylium (2), season phosphine positively charged ion (3), the quaternary ammonium cation (4), and structure is as follows:
Its negatively charged ion is selected from Cl
-, Br
-, I
-, AlCl
4 -, AlBr
4 -, AlI
4 -, CF
3COO
-, CH
3COO
-, CF
3SO
3 -, SCN
-, (CF
3SO
2)
2N
-, (CF
3SO
2)
3C
-, o-C
6H
4(OH) a kind of in (COO).
4. according to claim 3 described methods, it is characterized in that substituting group on (1), (2), (3) and (4) is selected from a kind of in alkane, halohydrocarbon, hydroxyl, aromatic hydrocarbons, the heterocycle hydro carbons, can be identical, also can be different, wherein the carbon number of aliphatic chain organic substituent group is between 1~14.
5. method according to claim 1, the temperature of the polyethylene terephthalate that it is characterized in that degrading is 50 ℃ to 250 ℃, preferred 120 ℃ to 200 ℃.
6. method according to claim 1, the polyethylene terephthalate time that it is characterized in that degrading is 6 hours to 24 hours.
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CN2007101757042A CN101250285B (en) | 2007-10-10 | 2007-10-10 | Method for degrading bis-hydroxyethyl terephthalate |
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CN101250285A true CN101250285A (en) | 2008-08-27 |
CN101250285B CN101250285B (en) | 2011-04-20 |
Family
ID=39953897
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102153443A (en) * | 2011-02-23 | 2011-08-17 | 合肥工业大学 | Method for degrading polyethylene terephthalate |
CN102516594A (en) * | 2011-11-04 | 2012-06-27 | 中国科学院长春应用化学研究所 | Recovery method of thermosetting epoxy resin or composite material thereof |
CN106065068A (en) * | 2016-07-27 | 2016-11-02 | 安徽泰达新材料股份有限公司 | Pure polyester used for powder coating and preparation method thereof |
JP2018508642A (en) * | 2014-12-23 | 2018-03-29 | イオニカ・テクノロジーズ・ベー・フェー | Improved reusable capture complex |
CN108690217A (en) * | 2017-04-07 | 2018-10-23 | 波音公司 | Carbon fiber recycles composition and method |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100487059C (en) * | 2005-01-20 | 2009-05-13 | 中国科学院过程工程研究所 | Method for preparing degradable material using stalk |
EP1994060A1 (en) * | 2006-03-08 | 2008-11-26 | Basf Se | Method for breaking down cellulose |
DE102006011075A1 (en) * | 2006-03-08 | 2007-09-13 | Basf Ag | Process for breaking down cellulose in solution |
-
2007
- 2007-10-10 CN CN2007101757042A patent/CN101250285B/en active Active
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102153443A (en) * | 2011-02-23 | 2011-08-17 | 合肥工业大学 | Method for degrading polyethylene terephthalate |
CN102153443B (en) * | 2011-02-23 | 2013-07-31 | 合肥工业大学 | Method for degrading polyethylene terephthalate |
CN102516594A (en) * | 2011-11-04 | 2012-06-27 | 中国科学院长春应用化学研究所 | Recovery method of thermosetting epoxy resin or composite material thereof |
JP2018508642A (en) * | 2014-12-23 | 2018-03-29 | イオニカ・テクノロジーズ・ベー・フェー | Improved reusable capture complex |
CN106065068A (en) * | 2016-07-27 | 2016-11-02 | 安徽泰达新材料股份有限公司 | Pure polyester used for powder coating and preparation method thereof |
CN106065068B (en) * | 2016-07-27 | 2017-10-27 | 安徽泰达新材料股份有限公司 | Powdery paints pure polyester and preparation method thereof |
CN108690217A (en) * | 2017-04-07 | 2018-10-23 | 波音公司 | Carbon fiber recycles composition and method |
US11377535B2 (en) | 2017-04-07 | 2022-07-05 | The Boeing Company | Carbon fiber recovery compositions and methods |
CN108690217B (en) * | 2017-04-07 | 2022-07-15 | 波音公司 | Carbon fiber recycling composition and method |
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CN101250285B (en) | 2011-04-20 |
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