[go: up one dir, main page]

CN116836191B - Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester - Google Patents

Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester Download PDF

Info

Publication number
CN116836191B
CN116836191B CN202310544293.9A CN202310544293A CN116836191B CN 116836191 B CN116836191 B CN 116836191B CN 202310544293 A CN202310544293 A CN 202310544293A CN 116836191 B CN116836191 B CN 116836191B
Authority
CN
China
Prior art keywords
pet
polyester
boric acid
acid ester
upgrading
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN202310544293.9A
Other languages
Chinese (zh)
Other versions
CN116836191A (en
Inventor
梅清清
张铭浩
阎炳会
余云开
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Zhejiang University ZJU
Original Assignee
Zhejiang University ZJU
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Zhejiang University ZJU filed Critical Zhejiang University ZJU
Priority to CN202310544293.9A priority Critical patent/CN116836191B/en
Publication of CN116836191A publication Critical patent/CN116836191A/en
Application granted granted Critical
Publication of CN116836191B publication Critical patent/CN116836191B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07FACYCLIC, CARBOCYCLIC OR HETEROCYCLIC COMPOUNDS CONTAINING ELEMENTS OTHER THAN CARBON, HYDROGEN, HALOGEN, OXYGEN, NITROGEN, SULFUR, SELENIUM OR TELLURIUM
    • C07F5/00Compounds containing elements of Groups 3 or 13 of the Periodic Table
    • C07F5/02Boron compounds
    • C07F5/025Boronic and borinic acid compounds
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C67/00Preparation of carboxylic acid esters
    • C07C67/03Preparation of carboxylic acid esters by reacting an ester group with a hydroxy group
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C68/00Preparation of esters of carbonic or haloformic acids
    • C07C68/06Preparation of esters of carbonic or haloformic acids from organic carbonates

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Catalysts (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

本发明公开了一种聚酯类材料解聚升级生成二元羧酸酯和硼酸酯的方法,涉及废旧资源综合利用和原材料的梯级利用。该方法使用非均相固体碱镁铝水滑石或其衍生复合氧化物催化PET甲醇解反应,随后苯硼酸原位捕获生成的乙二醇,经脱水环合形成不同类型的五元环状硼酸酯。本发明方法的产物为对苯二甲酸二甲酯和不同的五元环状硼酸酯。本发明可用于废旧PET材料的解聚升级,也可用于其他相似聚酯和聚碳酸酯,如聚己二酸乙二醇酯、聚丁二酸乙二醇酯和聚碳酸丙烯酯也适用于本发明回收策略,产物为相应的硼酸酯、丁二酸二甲酯和己二酸二甲酯。此外,反应中催化剂催化效率高,易分离回收,可重复利用,有效降低反应成本。

The invention discloses a method for depolymerizing and upgrading polyester materials to generate dicarboxylic acid esters and boric acid esters, and relates to the comprehensive utilization of waste resources and the cascade utilization of raw materials. The method uses a heterogeneous solid alkali magnesium aluminum hydrotalcite or a composite oxide derived therefrom to catalyze the methanolysis reaction of PET, and then phenylboronic acid captures the generated ethylene glycol in situ, and dehydrates and cyclizes to form different types of five-membered cyclic boric acid esters. The products of the method of the invention are dimethyl terephthalate and different five-membered cyclic boric acid esters. The invention can be used for the depolymerization and upgrading of waste PET materials, and can also be used for other similar polyesters and polycarbonates, such as polyethylene adipate, polyethylene succinate and polypropylene carbonate, which are also suitable for the recovery strategy of the invention, and the products are corresponding boric acid esters, dimethyl succinate and dimethyl adipate. In addition, the catalyst in the reaction has high catalytic efficiency, is easy to separate and recycle, can be reused, and effectively reduces the reaction cost.

Description

Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester
Technical Field
The invention relates to a method for producing dimethyl terephthalate and boric acid ester by depolymerizing and upgrading high-selectivity PET, which relates to comprehensive utilization of waste resources and cascade utilization of raw materials. More particularly, the present invention relates to a method for methanol depolymerizing of a variety of polyester raw materials and polycarbonates including PET, and obtaining high yields of dicarboxylic acid esters and a variety of five-membered cyclic boric acid esters.
Background
Polyethylene terephthalate (PET) is a polymer widely used in plastic packaging and fibers. The "disposable" nature and short service life (typically 6 months) of PET bottles make them the most common plastic waste, accounting for about 10% of the world's total. However, only 42% of the PET bottles are recycled, and the remaining 58% of the waste plastic is eventually thrown into landfills or burned. Currently, the main methods of processing PET are heat recovery, mechanical recovery, or chemical recovery, but only chemical recovery can convert the polymer into virgin monomer, fuel, or other value added product, extending the value chain and improving product quality. Chemical depolymerization of PET occurs by hydrolysis, alcoholysis, aminolysis or ammonolysis, which involves the selection of different nucleophiles to attack the c=o bonds in the polyester. However, the chemical depolymerization can be regarded as a monomer recovery strategy to some extent, and ethylene glycol produced simultaneously in the reaction is difficult to separate and recover due to the high boiling point characteristic and is usually abandoned. The ethylene glycol units of PET, however, also have a great potential for conversion to high value chemicals, and have been used for conversion of precursor materials to higher value-added small molecule carboxylic acids and light olefins. The innovative recycling of ethylene glycol units is therefore an important problem to be solved in the field of PET depolymerization at present.
Historically, most chemical recovery strategies have not been effectively implemented and eventually failed due to the low economic value of the derivative product. To advance the development of this field, it is important to simplify the monomer purification procedure and reduce the energy consumption. In various processing methods, PET methanolysis-derived dimethyl terephthalate (DMT) is more easily extracted and purified from the reaction system due to lower water solubility, making it a suitable alternative substrate for synthesizing recycled PET materials or other chemicals. Furthermore, the methanol decomposition system has a high contamination resistance, making it a cost-effective option for the treatment of complex PET-based waste materials. However, generally methanol decomposition requires relatively high temperatures (typically 200 ℃ C. Gtoreq.s.) to promote slow decomposition PET depolymerization reactions, and the product DMT yields are only between 80-85%. In order to pursue high yield of DMT, there are few research projects of supercritical methanol or microwave-assisted methanol decomposition systems, but the research projects are not advocated in consideration of equipment operation, economic benefit and the like. Furthermore, the use of homogeneous catalysts in most reactions results in difficulty in their separation from the system, causing additional economic costs, which also to some extent limit the industrial progress of the methanolysis of PET waste plastics. Therefore, developing a mild and efficient methanolysis strategy is important. Therefore, how to provide a means for reducing the cost of recycling catalyst in a PET methanol hydrolysis catalytic system, a directional upgrading recycle strategy of glycol in a depolymerization process and the catalyst in the catalytic system is a problem to be solved by those skilled in the art.
The cyclic borate is an important organic boron compound, and has been widely used in efficient construction of drugs and natural products due to the advantages of good functional group compatibility, simple preparation process of boric acid derivatives, low toxicity of boron byproducts, and the like. In addition, borates exhibit better chemoselectivity and regioselectivity than boric acid in some metal-catalyzed cross-coupling reactions (such as Heck and Suzuki reactions). In general, borates are obtained by reversible combination of glycol and boric acid, and thus, aryl boric acid can be used to capture EG components from waste PET, thereby achieving high value conversion of glycol while solving the glycol separation problem. The high-value recycling strategy is beneficial to complete comprehensive utilization of PET waste molecular layers, byproducts are only water, consumption of petroleum resources is relieved to a certain extent, and the recycling value of PET waste is improved.
Disclosure of Invention
Aiming at the requirements of PET waste plastic depolymerization and product directional upgrading and the defects existing in the prior art, the invention provides a method for depolymerizing and upgrading polyester materials to generate dicarboxylic acid esters and boric acid esters.
The specific technical scheme adopted by the invention is as follows:
a method for depolymerizing and upgrading polyester materials to generate dicarboxylic acid esters and boric acid esters comprises the following steps:
S1, placing a crushed polyester material, arylboronic acid, a heterogeneous catalyst and a methanol solvent into a reaction kettle, wherein the polyester material is polyethylene terephthalate (PET), polypropylene carbonate, polyethylene adipate or polyethylene succinate, the arylboronic acid is phenylboronic acid, p-methylphenylboronic acid, 3-methylphenylboronic acid or 4-fluorobenzeneboronic acid, and the heterogeneous catalyst is magnesium aluminum hydrotalcite or magnesium aluminum hydrotalcite derivative composite oxide which is baked at 350-600 ℃ and has a Mg/Al ratio of (4-1): 1;
And S2, carrying out depolymerization reaction on the reaction kettle at 160-200 ℃ for 1-4 hours, and cooling to room temperature after the reaction is finished to obtain a depolymerization product containing dicarboxylic acid ester and arylboric acid ester.
Taking PET as an example, the reaction formula of the depolymerization reaction can be expressed as:
preferably, the arylboronic acid is added in the same molar amount as the polyester-based material.
Preferably, the addition amount of the heterogeneous catalyst is 0.05-0.5 wt% of the polyester material.
Preferably, the addition amount of the methanol solvent is 3-6 mL/mmol of the polyester material.
Preferably, the polyester material is waste of polyethylene terephthalate (PET) material, and the waste is crushed into centimeter-level slices, particles or powder before being added into the reaction kettle, so that the recycling effect of the waste PET material can be ensured, and the dimethyl terephthalate and the Arylborate (ABE) can be obtained in a directional upgrading and high yield.
Preferably, the waste is in the form of PET waste bottles, PET matrix waste films, PET color strapping or PET non-woven fabrics.
Preferably, the roasting temperature of the heterogeneous catalyst is preferably 450-500 ℃.
Preferably, the roasting time of the heterogeneous catalyst is 4-8 hours.
Preferably, the Mg/Al ratio in the heterogeneous catalyst is preferably 4:1.
Preferably, the depolymerization temperature is 180 ℃.
Compared with the prior art, the invention has the following beneficial effects:
(1) The heterogeneous solid magnesium aluminum hydrotalcite derivative composite oxide catalyst adopted by the invention has the advantages of high efficiency, simple and convenient recovery and repeated cyclic utilization, and can promote the implementation of the methanolysis reaction of PET and the directional upgrading recovery of glycol in a short time.
(2) The waste plastic PET methanol depolymerization strategy developed by the invention has the advantages of short reaction time and high catalytic efficiency, and can finish the PET-DMT and glycol-borate directional conversion process with 99% yield under standard reaction conditions. The strategy has wide application range, various types of waste PET raw materials and various waste PET materials such as various PET waste bottles, PET matrix waste films, PET color binding ropes and PET non-woven fabrics can be used for efficiently finishing the directional upgrading conversion in a short time.
(3) The PET waste plastic matrix material can be replaced by various polyesters and polycarbonates with similar glycol units, such as polyethylene glycol succinate, polyethylene glycol adipate and polypropylene carbonate, so that the high applicability range of the strategy is displayed to a certain extent, the field range of waste plastic treatment materials is further widened, and corresponding conversion can be completed to obtain dicarboxylic acid ester and boric acid ester on the premise of ensuring high depolymerization efficiency and rapid reaction time.
Drawings
FIG. 1 is a graph showing the effect of recycling the catalyst of the present invention.
Detailed Description
The foregoing objects, features and advantages of the invention will be more readily apparent from the following detailed description of the invention. In the following description, numerous specific details are set forth in order to provide a thorough understanding of the present invention. The present invention may be embodied in many other forms than described herein and similarly modified by those skilled in the art without departing from the spirit of the invention, whereby the invention is not limited to the specific embodiments disclosed below. The technical features of the embodiments of the invention can be combined correspondingly on the premise of no mutual conflict.
Example 1
An autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller was charged with 0.192 g of PET powder (1 mmol), 0.13 g of p-methylphenylboric acid (1 mmol), 0.03 g of calcined commercial magnesium aluminum hydrotalcite (Mg/Al=3:1) and 5mL of methanol, and after the autoclave reactor was set, stirring and heating were started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 2h. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The obtained mixed solution was diluted with methylene chloride, and the yield of the diluted solution was measured by GC, and mesitylene was found to be an internal standard, which showed that the PET decomposition rate of this example was 100%, the yield of dimethyl terephthalate was 87%, and the yield of p-methylphenyl borate was 90%.
It should be noted that the catalyst in the invention is a composite oxide derived from magnesium aluminum hydrotalcite, but the ratio of Mg/Al can be controlled to change the catalytic performance, and the ratio of Mg/Al can be controlled to be (4-1): 1. Experiments show that the composite oxide with the Mg/Al ratio to be controlled to be 4:1 can achieve the optimal depolymerization reaction catalysis performance. In addition, in the experiment, the commercial hydrotalcite material can be used as a catalyst precursor, and the derivative composite oxide of the catalyst precursor can be synthesized by roasting to be used as a reaction catalyst. Another preferred method of preparing the magnesium aluminum hydrotalcite derived composite oxide catalyst is shown below by example 2.
Example 2
Preparation of heterogeneous catalyst magnesium aluminum hydrotalcite derived composite oxide (LDOs):
at a constant pH of 10, various hydrotalcites are prepared by a coprecipitation method, and then a magnesium-aluminum hydrotalcite derivative composite oxide (LDOs) is prepared by roasting. Firstly, two solutions are prepared, namely, a flask A is prepared, naNO 3.80 g (0.08 mol) is dissolved in 50mL of deionized water, a beaker B is prepared, 15.38g of Mg (NO 3)26H2 O (0.060 mol) and 5.63g of Al (NO 3)39H2 O (0.015 mol)) are dissolved in 50mL of deionized water, the content of the beaker B is added into the flask A in a dropwise manner, the pH value is kept to be 10 by using 1mol/L of NaOH solution in the dropwise process, the obtained mixed solution is reacted for two hours at the ambient temperature, then the mixed solution is heated to 80 ℃ for stirring and refluxing for 12 hours, the obtained precipitate is filtered, the mixture is washed by hot deionized water, then dried in a vacuum drying oven at 80 ℃ for 24 hours, and layered double hydroxide (Mg 4-Al1 -LDH) is obtained, specifically, the mixture is baked after the dried Mg 4-Al1 -LDH is ground into powder, the mixture is heated to 450 ℃ in an argon stream of a tubular furnace and kept for 4 hours and 500 ℃ for 4 hours, and the obtained composite magnesium oxide is kept in a tubular furnace for 4 ℃ for 4 hours, and the LDO-3 is a composite catalyst, namely, the composite magnesium oxide is obtained, and the composite catalyst is subjected to a heterogeneous phase is stored under the condition of LDO-3, and the LDO is a heterogeneous catalyst is used as a catalyst for the final catalyst.
Example 3
An autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller was charged with 0.192 g of CR-purity PET powder (1 mmol), 0.13 g of p-methylphenylboronic acid (1 mmol), 0.03 g of catalyst LDO-I and 5mL of methanol, and after the autoclave reactor was set, stirring and heating were started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 2h. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The obtained mixed solution was diluted with methylene chloride, and the yield of the diluted solution was measured by GC, and mesitylene was used as an internal standard, which revealed that the PET decomposition rate of this example was 100%, the yield of dimethyl terephthalate was 99%, and the yield of p-methylphenyl borate was 99%.
In addition, in order to prove the recycling property of the catalyst, the reacted catalyst LDO-I is separated and recovered, and is dried at 150 ℃ after being rinsed and decontaminated, so that the obtained heterogeneous solid magnesium aluminum hydrotalcite derivative composite oxide catalyst is directly recycled to the next reaction. The test results are shown in FIG. 1, and the yields of p-methylphenylborate and dimethyl terephthalate after repeated use for 6 times still reach 85% and 99%, respectively. After repeating for 6 times, the catalyst is heated to 450-500 ℃ again and baked, the catalytic effect of the catalyst can be basically recovered, and the yields of the p-methylphenyl borate and the dimethyl terephthalate are respectively 98% and 99% when depolymerization is carried out after recovery.
Example 4
Waste PET plastic bottles (brands such as cola, coca-cola and farmer mountain spring) are crushed in centimeter level in advance, then an autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller is filled with centimeter level crushed materials (1 mmol) of 0.192 g PET plastic bottle, 0.13 g p-toluylboronic acid (1 mmol), 0.03 g catalyst LDO-I and 5mL methanol, and after the autoclave reactor is placed, stirring and heating are started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 3h. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The obtained mixed solution was diluted with methylene chloride, and the yield of the diluted solution was measured by GC, and mesitylene was used as an internal standard, which revealed that the PET decomposition rate of this example was 100%, the yield of dimethyl terephthalate was 99%, and the yield of p-methylphenyl borate was 99%.
Example 5
An autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller was charged with 0.192 g of PET powder (1 mmol), 0.136 g of 3-methylphenylboronic acid (1 mmol), 0.03 g of catalyst LDO-I and 5mL of methanol, and after the autoclave reactor was set, stirring and heating were started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 2h. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The resulting mixture was diluted with methylene chloride, and the yield of the diluted solution was measured by GC, and mesitylene was found to be an internal standard, which indicated that the PET decomposition rate of this example was 100%, the yield of dimethyl terephthalate was 99%, and the yield of 3-methylphenylborate was 99%.
Example 6
An autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller was charged with 0.192 g of PET powder (1 mmol), 0.139 g of 4-fluorobenzeneboronic acid (1 mmol), 0.03 g of catalyst LDO-I and 5mL of methanol, and after the autoclave reactor was set, stirring and heating were started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 2h. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The obtained mixed solution was diluted with methylene chloride, and the yield of the diluted solution was measured by GC, and mesitylene was used as an internal standard, which revealed that the PET decomposition rate of this example was 100%, the yield of dimethyl terephthalate was 99%, and the yield of p-fluorobenzeneborate was 99%.
Example 7
An autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller was charged with 0.102 g of polypropylene carbonate particles (1 mmol), 0.136 g of p-methylphenylboronic acid (1 mmol), 0.03 g of catalyst LDO-I and 5mL of methanol, and after the autoclave reactor was set, stirring and heating were started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 2h. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The resulting mixture was diluted with methylene chloride, and the yield of the diluted solution was measured by GC with mesitylene as an internal standard, and the result showed that the polypropylene carbonate particles of this example had a decomposition rate of 100% and produced dimethyl carbonate and p-methylphenyl borate, and the yield of p-methylphenyl borate was 95%.
Example 8
An autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller was charged with 0.172 g of polyethylene glycol adipate (1 mmol), 0.136 g of p-methylphenylboronic acid (1 mmol), 0.03 g of catalyst LDO-I and 5mL of methanol, and after the autoclave reactor was set, stirring and heating were started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 2h. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The obtained mixed solution was diluted with methylene chloride, and the yield of the diluted solution was measured by GC, and mesitylene was used as an internal standard, which revealed that the decomposition rate of polyethylene glycol adipate of this example was 100%, the yield of dimethyl adipate was 98%, and the yield of p-methylphenyl borate was 99%.
Example 9
An autoclave reactor equipped with an electromagnetic stirrer, a thermocouple and a program temperature controller was charged with 0.144 g of polyethylene succinate (1 mmol), 0.136 g of p-methylphenylboronic acid (1 mmol), 0.03 g of catalyst LDO-I and 5mL of methanol, and after the autoclave reactor was set, stirring and heating were started. The reaction system was warmed to 180 ℃ and reacted at that temperature for 1 hour. After the reaction is completed, the temperature is reduced to room temperature, and the obtained mixed solution is the product. The obtained mixed solution was diluted with methylene chloride, and the yield of the diluted solution was measured by GC, and mesitylene was used as an internal standard, and the result showed that the decomposition rate of polyethylene glycol succinate in this example was 100%, the yield of dimethyl succinate was 88%, and the yield of p-methylphenyl borate was 99%.
The above embodiment is only a preferred embodiment of the present invention, but it is not intended to limit the present invention. Various changes and modifications may be made by one of ordinary skill in the pertinent art without departing from the spirit and scope of the present invention. Therefore, all the technical schemes obtained by adopting the equivalent substitution or equivalent transformation are within the protection scope of the invention.

Claims (7)

1. A method for depolymerizing and upgrading polyester materials to generate dicarboxylic acid esters and boric acid esters is characterized by comprising the following steps:
S1, placing crushed polyester materials, arylboronic acid, heterogeneous catalyst and methanol solvent into a reaction kettle; wherein the polyester material is polyethylene terephthalate (PET), polypropylene carbonate, polyethylene adipate or polyethylene succinate; the preparation method comprises the steps of dissolving 6.80g of NaNO 3 in 50mL of deionized water to obtain a first solution, dissolving 15.38g of Mg (NO 3)26H2 O and 5.63g of Al (NO 3)39H2 O) in 50mL of deionized water to obtain a second solution, dropwise adding the second solution into the first solution, reacting the obtained mixed solution for two hours at the ambient temperature by using a NaOH solution with the pH value of 1mol/L in the dropwise adding process, heating the mixed solution to 80 ℃ for stirring and refluxing for 12 hours, filtering the obtained precipitate, washing the precipitate with hot deionized water, drying the washed precipitate in a vacuum drying box with the temperature of 80 ℃ for 24 hours to obtain layered double hydroxide, grinding the dried layered double hydroxide into powder, heating the layered double hydroxide in an argon flow of a tubular furnace to 450 ℃ and maintaining the temperature for 4 hours, and heating the layered double hydroxide to the temperature for 500 ℃ for maintaining the magnesium oxide for another 500 ℃ to obtain the calcined composite oxide;
S2, carrying out depolymerization reaction for 1-4 hours at a depolymerization temperature of 160-200 ℃ on the reaction kettle, and cooling to room temperature after the reaction is finished to obtain a depolymerization product containing dicarboxylic acid ester and arylboric acid ester;
The dicarboxylic acid ester is dimethyl terephthalate, dimethyl carbonate, dimethyl adipate or dimethyl succinate;
the aryl borate is 3-methyl phenyl borate, p-fluoro phenyl borate or p-methyl phenyl borate.
2. The method for upgrading a polyester-based material to dimethyl terephthalate and boric acid esters according to claim 1, wherein the arylboronic acid is added in the same molar amount as the polyester-based material.
3. The method for upgrading a polyester-based material to produce dimethyl terephthalate and boric acid ester according to claim 1, wherein the heterogeneous catalyst is added in an amount of 0.05 wt% -0.5 wt% of the polyester-based material.
4. The method for producing dimethyl terephthalate and boric acid ester by upgrading a polyester material according to claim 1, wherein the addition amount of the methanol solvent is 3-6 mL/mmol of the polyester material.
5. The method for upgrading a polyester material to produce dimethyl terephthalate and boric acid ester according to claim 1, wherein the polyester material is waste of polyethylene terephthalate (PET) material, and the waste is crushed into a centimeter-level flake, granule or powder before being added into a reaction kettle.
6. The method for upgrading a polyester-based material to dimethyl terephthalate and boric acid ester according to claim 5, wherein the waste is in the form of PET waste bottles, PET matrix waste films, PET color strapping or PET nonwoven fabrics.
7. The method for upgrading a polyester-based material to dimethyl terephthalate and boric acid esters according to claim 1, wherein the depolymerization temperature is 180 ℃.
CN202310544293.9A 2023-05-15 2023-05-15 Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester Active CN116836191B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310544293.9A CN116836191B (en) 2023-05-15 2023-05-15 Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310544293.9A CN116836191B (en) 2023-05-15 2023-05-15 Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester

Publications (2)

Publication Number Publication Date
CN116836191A CN116836191A (en) 2023-10-03
CN116836191B true CN116836191B (en) 2025-01-14

Family

ID=88167786

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310544293.9A Active CN116836191B (en) 2023-05-15 2023-05-15 Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester

Country Status (1)

Country Link
CN (1) CN116836191B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN117603036B (en) * 2023-11-22 2025-02-25 浙江大学 A method for hydrolyzing waste PET polyester by CO2 catalysis

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1304924A (en) * 2000-07-07 2001-07-25 中国科学院山西煤炭化学研究所 Process for depolymerizing waste glycol tere-phthalate
BR102018068454B1 (en) * 2018-09-12 2022-04-19 Petróleo Brasileiro S.A. - Petrobras CATALYSTS AND PROCESS FOR OBTAINING RECYCLED POLYESTER

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
Full valorisation of waste PET into dimethyl terephthalate and cyclic arylboronic esters;Minghao Zhang et al.;《Applied Catalysis B: Environment and Energy》;20240407;第352卷;第1-8页 *

Also Published As

Publication number Publication date
CN116836191A (en) 2023-10-03

Similar Documents

Publication Publication Date Title
Wang et al. Sodium titanium tris (glycolate) as a catalyst for the chemical recycling of poly (ethylene terephthalate) via glycolysis and repolycondensation
CN117603043B (en) A method for upgrading polyester materials to dicarboxylic acid esters and ethylene carbonate
CN116836191B (en) Method for depolymerizing and upgrading polyester material to generate dicarboxylic acid ester and boric acid ester
CN113173856A (en) Method for catalytic degradation of waste polyester material by using zinc catalyst
KR102126236B1 (en) Method for producing dioctylterephthalate and antifreeze simultaneously by using polyethyleneterephthalate
CN111018710A (en) A kind of preparation method of dimethyl carbonate
CN117986114B (en) A method for alkylating polyester materials with the participation of carbonate or carboxylate
CN107400243B (en) Preparation method of zirconium-based microporous coordination polymer
CN116635462A (en) Depolymerization catalyst for polymers comprising ester functional groups and depolymerization method using the depolymerization catalyst
CN104447341B (en) A kind of polyester alcoholysis method
CN1934177A (en) Method of decomposing plastic
CN113117748A (en) Bicyclic guanidine salt eutectic solvent catalyst and preparation method and application thereof
CN111217700A (en) Method for catalyzing alcoholysis of polyethylene terephthalate by using non-metal choline ionic liquid
Yuan et al. Metal− organic frameworks as recyclable catalysts for efficient esterification to synthesize traditional plasticizers
CN108837847A (en) The catalyst and method of alcohol polylactic acid
CN102250449A (en) Process for synthesizing saturated polyester resin by using recycled terephthalic acid
CN111484395A (en) Method for recovering bisphenol A by catalyzing polycarbonate to carry out methanol alcoholysis by composite metal oxide
CN117339593B (en) Magnetic solid base catalyst and method for directional upgrading of methanolysis of polyester materials
CN108947798A (en) A kind of method of degradation polymer
CN117603044B (en) Method for depolymerizing and upgrading polyester into carboxylate and borate by using ionic liquid to catalyze
CN110951063B (en) Catalyst composition for preparing polyester and preparation method of polyester
CN1100614C (en) Solid catalyst for synthesizing glycol monoether acetate
CN114907211A (en) A kind of degradation method of polyester
CN114230857A (en) Method for rapidly degrading PET through high-temperature swelling effect
CN117645534B (en) Method for preparing dicarboxylic acid and aniline by synergistic treatment of waste polyester and nitrobenzene

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant