• 专利附录
  • 专利说明
  • 权利要求
  • 类似技术
  • 同族专利
  • 引用文献
  • 法律状态
  • 优先权
    • 专利摘要:
    The invention relates to a process for the depolymerization of a polyester filler comprising opaque PET, said process comprising at least the steps of conditioning, depolymerization, separation of the diol and separation of the effluent rich in liquid monomers, followed a fading step.
    公开号:FR3053691A1
    申请号:FR1656423
    申请日:2016-07-05
    公开日:2018-01-12
    发明作者:Cyprien Charra；Frederic Favre；Adrien Mekki-Berrada；Olivier Thinon
    申请人:IFP Energies Nouvelles IFPEN；
    IPC主号:
    专利说明:

    TECHNICAL FIELD OF THE INVENTION
    The invention relates to a process for depolymerizing a polyester, in particular polyester terephthalate, with a view to recycling it in a polymerization unit.
    PRIOR ART
    The chemical recycling of polyethylene terephthalate (PET) has been the subject of numerous studies aimed at breaking down the recovered PET into waste monomers which can again be used as feedstock for a polymerization process.
    Many polyesters come from material collection and sorting circuits. In particular, PET can come from the collection of bottles, trays, films, resins and / or fibers made up of PET. Polyester from collection and recycling channels is called recycled polyester.
    Recycled PET can be classified into four main categories:
    - clear PET, consisting mainly of transparent colorless PET (generally at least 60% by weight) and brightly colored PET, which does not contain pigments and can be sent to mechanical recycling processes,
    - dark or colored PET (green, red, etc.), which can generally contain up to 0.1% by weight of dyes or pigments but remains transparent, or translucent,
    - opaque PET, which contains a significant quantity of pigments at levels typically varying between 0.25 and 5% by weight, used to opacify the polymer, used more and more for example for the manufacture of food containers, such as milk bottles , in the composition of cosmetic, phytosanitary or coloring bottles.
    - multilayered PET, which includes layers of plastics other than PET or a layer of recycled PET between layers of virgin PET, that is to say that it has not been recycled, or an aluminum film for example. This PET is used after thermoforming to make packaging such as trays.
    The collection channels for supplying recycling channels are structured differently depending on the country. They evolve in order to maximize the quantity of plastic recovered in the waste depending on the nature and the quantity of sorting flows and technologies.
    The recycling process for these different streams generally consists of a first stage of packaging in the form of straw in which raw packaging bales are washed, purified and sorted, crushed then again purified and sorted to produce a stream of flakes generally containing less than 2% of impurities (glass, metals, other plastics, wood, cardboard, mineral elements), preferably less than 1% of impurities.
    The clear PET flakes can then undergo an extrusion-filtration step allowing the production of extrudates which are then reusable in mixture with virgin PET to make new products (bottles, fibers, films). A solid state vacuum polymerization step (known by the acronym SSP) is necessary for food use. This type of recycling is called mechanical recycling.
    The dark or colored PET flakes are also mechanically recyclable. However, the coloring of the extrudates formed from the colored fluxes limits the uses and this PET is most often used to produce fibers or packaging strips. The outlets are therefore more limited.
    The presence of opaque PET containing high levels of pigments poses problems for recyclers because opaque PET alters the mechanical properties of recycled PET. Opaque PET is currently collected with colored PET and ends up in the colored PET stream. Given the development of uses for opaque PET, the contents of opaque PET in the flow of colored PET are currently between 5-10% and are increasing. In a few years, it will be possible to reach opaque PET contents in the flow of colored PET greater than 20%. However, it has been shown that beyond 10-15% of opaque PET in the flows of colored PET, the mechanical properties of recycled PET are altered and prevent recycling in the form of fibers, the main outlet of the sector for the Colorful PET.
    The main pigments used are metal oxides such as TiO 2 , CoAI 2 0 4 , Fe 2 O 3 , silicates, polysulfides, and carbon black. Pigments are particles generally between 0.1 and 10 µm in size, and mostly between 0.4 and 0.8 µm. The total elimination of these pigments by filtration, necessary to consider recycling opaque PET, is technically difficult. Indeed, on the one hand these particles are extremely clogging, on the other hand certain pigments are known to catalyze the polymerization reaction of PET under the operating conditions of the separation operations, which increases the risks of clogging of the filters with the polymers products within said filters.
    The dyes used are of different natures and often contain heteroatoms of type O and N, and conjugated unsaturations, such as, for example, quinone, methine, azo functions, or molecules such as pyrazolone and quinophthalone.
    The recycling of colored or opaque PET is therefore extremely delicate.
    Patent EP0865464 describes a process for recycling by depolymerization of polyesters comprising the steps of depolymerization in the presence of a diol, evaporation of the diol, dissolution of the mixture in a hot solvent, filtration and precipitation of the filtered solution, precipitate which can then be used for the preparation of a new polymer. This document describes that the monomers and oligomers can be separated in a scraped film evaporator (thin film evaporator according to the English term), without however specifying under what conditions this evaporator must be operated. This patent also does not address the issues related to the nature of the PET treated.
    Patent JP3715812 describes the production of refined BHET from PET. The depolymerization is followed by a pre-purification step by cooling, filtration, adsorption and treatment on ion exchange resin, presented as very important, carried out before the evaporation of the glycol and the purification of the BHET. Pre-purification avoids the re-polymerization of BHET in the subsequent purification steps. This process works perfectly as long as the load contains solid impurities which are easy to separate (plastics other than PET, solid residues). On the other hand, the passage through a filtration step and ion exchange resin is extremely problematic when the charge comprises a large quantity of very small solid particles, like pigments, which is the case when the treated charge comprises Opaque PET, in particular in substantial proportions (more than 10% by weight of opaque PET).
    Patent EP0865464 describes recycling by depolymerization of polyesters with a diol, followed by a step of evaporation of the diol, then by dilution in a hot solvent. This hot dilution makes it possible to separate impurities larger than 50 μm by filtration. The treated solution is then cooled and the precipitated components repolymerized. The filtration step removes insoluble impurities. The low proportion of pigments in colored PET allows separation by filtration. However, this technology could not work with the quantity of pigments present in opaque PET, these pigments quickly clogging the filter.
    Patent FR2103115 deals with the purification of BHET by distillation with a very short residence time in order to avoid the repolymerization of BHET, mainly with a view to eliminating the impurities resulting from the reaction of terephthalic acid and of oxide d 'ethylene. This document teaches that it is relevant to effect the separation of BHET at a relatively high temperature (200-350 ° C) in order to minimize the residence time in the distillation. This document does not deal with the presence of other solid impurities, such as pigments. However, at high temperature, these pigments will largely promote the polymerization of BHET.
    OBJECT AND INTEREST OF THE INVENTION
    The subject of the invention is a process for depolymerizing a polyester filler comprising opaque PET, said process comprising at least the following steps:
    a) a conditioning step supplied with said polyester filler;
    b) a glycolysis depolymerization step fed at least with the effluent from the step
    a) and by adding diol, operated at a temperature between 200 and 400 ° C., with from 1 to 20 moles of diol per mole of diester in said polyester filler and a residence time of the polyester of between 0.1 and 5 a.m .;
    c) a step for separating the diol fed at least with the effluent from step b), operated at a temperature between 100 and 250 ° C., at a pressure lower than that of the step
    b) and producing an effluent diol and an effluent rich in liquid monomers;
    d) a step of separating the effluent rich in liquid monomers from step c) into an effluent heavy impurities and a pre-purified monomer effluent operated at a temperature below 250 ° C and a pressure below 0.001 MPa with a liquid residence time of less than 10 min and
    e) a step of bleaching the pre-purified monomer effluent, carried out at a temperature between 100 and 250 ° C., and at a compressed pressure between 0.1 and 1.0 MPa in the presence of an adsorbent and producing a purified monomer effluent.
    One advantage of the invention is to be able to process polyesters comprising pigments and dyes, in particular azure, colored, opaque or even multi-layer PET.
    The process according to the invention, capable of treating opaque PET, makes it possible to remove the pigments and dyes and return to the monomer by chemical reaction. This monomer is then repolymerized into a polymer which has no difference with a polyester, in particular a virgin PET, thus allowing all uses of virgin PET.
    DETAILED DESCRIPTION OF THE INVENTION
    Charge
    The process according to the invention is powered by a polyester filler comprising at least one polyester, that is to say a polymer whose repeating unit of the main chain contains an ester function and comprising opaque polyethylene terephthalate (PET). Said polyester filler advantageously consists of recycled polyesters.
    PET, called polyethylene terephthalate or poly (ethylene terephthalate), is a polymer obtained by the polycondensation of terephthalic acid (PTA) with ethylene glycol of chemical formula:
    where n represents the number of units in the PET. In the following text, the term “moles of diester” in said polyester filler means the number of moles of motif - [0-CO-O- (C 6 H 4 ) CO-O-CH 2 -CH 2 ] -, which is the diester unit resulting from the reaction of PTA and ethylene glycol, in the PET included in said polyester filler.
    Preferably, said polyester filler comprises at least one PET chosen from opaque, dark, multilayer PET and their mixture. More preferably, said polyester filler comprises at least 10% by weight of opaque PET, very preferably at least 15% by weight of opaque PET, said opaque PET advantageously being recycled opaque PET.
    Said filler advantageously comprises from 0.1% to 10% by weight of pigment, advantageously from 0.1 to 5% by weight. It advantageously comprises from 0.05% to 1% of dyes, advantageously from 0.05 to 0.2% by weight.
    Said polyester filler can also comprise up to 2% by weight of impurities such as metals, other plastics (PP, HDPE ...), cardboard or paper, wood or minerals ... The polyester filler can also include elements used as a polymerization catalyst and as stabilizers in PET production processes, such as antimony, titanium, tin.
    The polyesters, advantageously recycled, included in said filler are advantageously washed and ground so as to form a polyester filler consisting of flakes whose greatest maximum length is less than 10 cm, preferably between 5 and 25 mm.
    Step a) of conditioning
    Said method according to the invention comprises a step a) of conditioning supplied by said polyester filler.
    Said step a) makes it possible to heat and pressurize said polyester filler under the operating conditions of step b) of depolymerization.
    The charge is gradually heated to a temperature above its melting temperature so as to become liquid. Advantageously, at least 80% by weight of the filler is in liquid form at the end of step a), very advantageously at least 90% by weight, preferably at least 95% by weight at the end of step a). The temperature of said step a) is advantageously between 225 and 275 ° C. This temperature is kept as low as possible to minimize the thermal degradation of the polyester.
    Advantageously, said step a) comprises a screw conveying section, called an extrusion section, supplied by said polyester filler.
    The residence time in said extrusion section, defined as the volume of said section divided by the volume flow rate of charge is advantageously less than 15 min, preferably less than 10 min, and preferably less than 2 min.
    Said extrusion section is advantageously connected to a vacuum extraction system so as to remove impurities such as dissolved gases, light organic compounds and / or moisture present in the feed. Said extrusion section may also advantageously comprise a filtration system for removing solid particles of size greater than 40 μm, preferably of size between 3 and 40 μm, such as particles of sand.
    Said polyester filler is advantageously brought into contact with at least a fraction of the diol effluent from step c), advantageously within said extrusion section. This contacting has the effect of initiating the depolymerization reaction before the introduction into step b) of depolymerization. In this case, we speak of a reactive extrusion section.
    The diol effluent from step c) can advantageously be overheated prior to feeding it in step a) in order to facilitate the heating of the polyester filler. The number of moles of diol originating from step c) per mole of diester in said polyester filler is advantageously less than 1.0 and preferably less than 0.5.
    Said polyester filler can also advantageously be supplied with a mixture of a fraction of the heavy impurities effluent from step d), said fraction having preferably been purified in a filtration step.
    Step b) of depolymerization
    The method according to the invention comprises a depolymerization step by glycolysis fed at least by the effluent from said step a) and by an addition of diol, operated at a temperature between 200 and 400 ° C, preferably between 230 and 350 ° C, preferably between 250 ° C and 300 ° C, in the liquid phase, with 1 to 20 moles of diol per mole of diester in said polyester filler, preferably 3 to 15, and preferably 5 to 10 moles per mole, and a residence time in said step b) between 0.1 and 5 h preferably between 0.5 and 3 h.
    The operating pressure of said step b) is determined so as to maintain the reaction system in the liquid phase. This pressure is at least 0.1 MPa, preferably at least 0.4 MPa. By reaction system is meant all of the compounds and phases present in said step b) derived from the feed of said step.
    The residence time is defined as the ratio of the volume of liquid in said reaction section to the sum of the volume flow rate of the polyester filler and the diol make-up.
    The diol is advantageously monoethylene glycol.
    Said step b) of depolymerization advantageously comprises one or more reaction sections. Each reaction section can be implemented in any type of reactor known to a person skilled in the art making it possible to carry out a depolymerization or trans-esterification reaction, preferably in a reactor stirred by a mechanical stirring system or / and by recirculation loop or / and by fluidization. Said reactor may include a conical bottom for purging the impurities.
    The glycolysis reaction can be carried out with or without the presence of a catalyst. When the glycolysis reaction is carried out in the presence of a catalyst, the latter can be homogeneous or heterogeneous and chosen from the esterification catalysts known to those skilled in the art such as the oxide and salt complexes of antimony, tin , of titanium, the metal alkoxides of groups (I) and (IV) of the periodic table, organic peroxides, acid-base metal oxides.
    A preferred heterogeneous catalyst advantageously comprises at least 50% by mass relative to the total mass of the catalyst, preferably at least 70% by mass, advantageously at least 80% by mass, very advantageously at least 90% by mass, and even more advantageously at least 95 % mass of a solid solution consisting of at least one spinel of formula Z X AI 2 O (3 + X ) in which x is between 0 (limit excluded) and 1, and Z is chosen from Co, Fe, Mg , Mn, Ti, Zn, and comprising at most 50% by mass of alumina and of oxide of element Z. Said preferred heterogeneous catalyst advantageously contains at most 10% by mass of dopants chosen from silicon, phosphorus and boron taken alone or as a mixture. For example, and in a nonlimiting manner, said solid solution can consist of a mixture of spinel ZnAI 2 O 4 and spinel CoAI 2 0 4 , or else consist of a mixture of spinel ZnAI 2 O 4 , spinel MgAI 2 O 4 and spinel FeAI 2 O 4 , or else consist only of spinel ZnAI 2 O 4 .
    The particular arrangement in which said preferred heterogeneous catalyst is used has the advantage of an excellent conversion of PET by glycolysis to BHET. In addition, the heterogeneous catalyst of this particular arrangement has the surprising property of capturing impurities, in particular dyes, additives and catalytic substances used for the polymerization and present in the PET treated in the process according to the invention, such as antimony, magnesium, manganese, zinc, titanium, phosphorus, which simplifies the subsequent stages of purification of BHET with a view to its reuse in a polymerization process.
    Preferably, said depolymerization step is carried out without a catalyst.
    Said depolymerization step is advantageously carried out in the presence of a solid adsorbent agent in powder or shaped form, the function of which is to capture at least part of the colored impurities, thereby relieving step e) of discoloration. Said solid adsorbent agent is advantageously an activated carbon.
    The glycolysis reaction makes it possible to convert the polyester filler into monomers and ester oligomers, advantageously PET into Bis (2-Hydroxyethyl) terephthalate (BHET) monomer and BHET oligomers. The conversion of the polyester filler in said depolymerization step is greater than 50%, preferably greater than 70%, more preferably greater than 85%. The molar yield of BHET is greater than 50%, preferably greater than 70%, preferably greater than 85%. The molar yield of BHET corresponds to the molar flow rate of BHET at the outlet of said step b) over the number of moles of diester in the polyester filler feeding said step b).
    An internal recirculation loop is advantageously implemented in step b), that is to say the withdrawal of a fraction from the reaction system, the filtration of this fraction, and the reinjection of said fraction in said step b ). This internal loop makes it possible to eliminate the solid impurities possibly included in the reaction liquid.
    Step c) separation of the diol
    The method according to the invention comprises a step for separating the diol fed at least with the effluent from step b), operated at a temperature between 100 and 250 ° C., at a pressure lower than that of step b ) and producing an effluent diol and an effluent rich in liquid monomers.
    The main function of step c) is to recover all or part of the unreacted diol.
    Stage c) is operated at a pressure lower than that of stage b) so as to vaporize a fraction of the effluent of stage b) into a gas effluent and a liquid effluent. Said liquid effluent constitutes the effluent rich in liquid monomers. The gas effluent, consisting of more than 50% by weight of diol, preferably more than 70% by weight, preferably more than 90% by weight, constitutes a gaseous diol effluent which is condensed into said effluent diol.
    Step c) is advantageously implemented in a succession of gas-liquid separation sections, advantageously from 1 to 5 successive separation sections, very advantageously from 3 to 5 successive separations. The liquid effluent from the anterior section feeds the subsequent section. All of the gas effluents are condensed to form the diol effluent. The liquid effluent from the last gas-liquid separation section constitutes the effluent rich in liquid monomers.
    The temperature and pressure of the subsequent section are lower than those of the previous section so that the gas effluent leaving the front section can, by condensing, reboil part of the liquid effluent from the subsequent section. In this configuration, the heat input to recover the diol is minimized.
    Step c) is carried out so that the temperature of the liquid effluents is maintained above the value below which the polyester monomer precipitates, and below a high value, depending on the molar ratio of diol / monomer , above which the monomer re-polymerizes significantly. The temperature in step c) is between 100 and 250 ° C, preferably between 110 and 220 ° C, preferably between 120 and 210 ° C. The operation in a succession of gas-liquid separations, advantageously in a succession of 1 to 5, preferably of 3 to 5 successive separations, is particularly advantageous because it makes it possible to adjust in each separation the temperature of the liquid effluent corresponding to the above constraints, which is particularly important due to the presence of opaque PET in the polyester filler, the pigments used to opacify the PET can have a catalytic action in the polymerization reaction of PET.
    The pressure in step c) is adjusted to allow the diol to evaporate at a temperature minimizing re-polymerization and allowing optimal energy integration. It is generally between 0.00001 and 0.2 MPa, preferably between 0.00004 and 0.15 MPa, preferably between 0.00004 and 0.1 MPa.
    The separation section (s) are advantageously agitated by any method known to those skilled in the art.
    The effluent diol may contain other compounds such as dyes, light alcohols, water, diethylene glycol. At least a fraction of the diol effluent is advantageously recycled to step a) and / or step b), advantageously in admixture with a make-up of diol external to the process according to the invention.
    All or part of said diol effluent can be treated in a purification step prior to its recycling to steps a) and / or b) and / or its use as a mixture in step d). This purification step may include, without being exhaustive, adsorption on a solid (for example on activated carbon) to remove the dyes and one or more distillations to separate the impurities such as diethylene glycol, water and other alcohols.
    Step d) of separation of the monomer
    The method according to the invention comprises a step d) of separating the effluent rich in monomers from step c) into an effluent heavy impurities and a pre-purified monomer effluent operated at a temperature below 250 ° C, preferred way less than
    230 ° C, and very preferably less than 200C, and a pressure less than 0.001 MPa, preferably less than 0.0005 MPa with a liquid residence time less than 10 min, preferably less than 5 min, preferably less than 1 min.
    The purpose of this separation step is to separate the monomer, which is vaporized, from the oligomers and from the polyester which remain liquid and therefore capture the heavy impurities, in particular the pigments, from the unconverted polymer, from the other polymers possibly present and from the polymerization catalysts. , minimizing the loss of monomers by repolymerization. Some oligomers can be entrained with the monomer.
    The total removal of pigments by filtration is particularly difficult because of the very small size of said pigments.
    Due to the possible presence in the polyester feed of polymerization catalysts, in particular if this feed comprises opaque PET, this separation must be carried out with very short liquid residence times and at a temperature not exceeding 250 ° C. Separation by simple atmospheric distillation is therefore not possible. Certain pigments used to opacify PET, such as TiO 2 , are known to catalyze the polymerization reaction.
    Step d) of separation is advantageously implemented in a falling film or scraped film evaporation system or by short-path distillation with falling film or scraped film. The very low operating pressure is necessary in order to be able to operate step d) at a temperature below 250 ° C., preferably below 230 ° C. while allowing the vaporization of the monomer.
    A polymerization inhibitor is advantageously mixed with the effluent rich in liquid monomers before being fed in said step d).
    A fluxing agent is advantageously mixed with the effluent rich in liquid monomers before being fed in said step d) so as to facilitate the elimination of heavy impurities, in particular pigments, at the bottom of the short-path evaporation or distillation system. . This fluxing agent must have a boiling temperature much higher than the BHET under the operating conditions of step d). It can be, for example, polyethylene glycol, or PET oligomers.
    Said heavy impurities effluent includes in particular pigments, oligomers and unseparated BHET. A fraction of said heavy impurities effluent can advantageously be recycled to stage a) of conditioning and supply and / or to stage b) of depolymerization.
    Said heavy impurities effluent advantageously undergoes at least one purification step, preferably a filtration step before its recycling so as to reduce the quantity of pigments and / or other solid impurities. All or part of said heavy impurities effluent can also advantageously be purged from the process and sent to an incineration system.
    A fraction of the diol effluent can advantageously be mixed with the heavy impurities effluent from step d) so as to reduce the viscosity of said heavy impurities effluent and facilitate its transport to step a) and / or step b), and possibly its treatment in an optional filtration step.
    Said pre-purified monomer effluent is advantageously sent to a gas-liquid separation section, operated in any equipment known to those skilled in the art, at a temperature between 100 and 250 ° C., preferably between 110 and 200 ° C., and preferably between 120 and 180 ° C, and at a compressed pressure between 0.00001 and 0.1 MPa, preferably between 0.00001 and 0.01 MPa, and preferably between 0.00001 and 0.001 MPa. Said separation section makes it possible to separate a gaseous diol effluent and a liquid pre-purified monomer effluent. Said gas-liquid separation makes it possible to further reduce the amount of diol remaining in the pre-purified monomer effluent by recovering in said gaseous diol effluent more than 50% by weight, preferably more than 70% by weight, preferably more than 90% by weight of the diol entrained in step d) with the pre-purified monomer effluent. The amount of monomer entrained in said effluent diol gas is preferably less than 1% by weight, preferably less than 0.1% by weight and more preferably less than 0.01% by weight of the amount of monomer present in the monomer effluent pre-purified. Said gaseous diol effluent is then advantageously condensed, optionally pretreated in a purification step and recycled with the diol effluent from step c) to step a) and / or step b) and / or mixed in step d).
    Step e) discoloration
    The method according to the invention comprises a step of bleaching the pre-purified monomer effluent, carried out at a temperature between 100 and 250 ° C, preferably between 110 and 200 ° C, and preferably between 120 and 180 ° C, and at a pressure between 0.1 and 1.0 MPa, preferably between 0.2 and 0.8 MPa, and preferably between 0.3 and 0.5 MPa in the presence of an adsorbent and producing a purified monomer effluent.
    Said adsorbent can be any adsorbent known to a person skilled in the art capable of capturing the dyes, such as activated carbon, clays, advantageously an activated carbon.
    The pre-purified monomer effluent is advantageously mixed with a fraction of the diol effluent from step c) or with a make-up of diol external to the process according to the invention.
    The purified monomer effluent advantageously feeds a polymerization step known to those skilled in the art with a view to producing PET which nothing distinguishes from virgin PET, advantageously downstream of the supply of ethylene glycol, terephthalic acid or dimethyl terephthalate according to the polymerization step selected. The supply of the purified monomer effluent in a polymerization stage makes it possible to reduce the supply of dimethyl terephthalate or terephthalic acid by an equivalent flow rate.
    EXAMPLES
    EXAMPLE 1 - CONFORM
    This example illustrates the use of the process according to the invention with a filler comprising 20% by weight of opaque PET.
    kg / h of flakes from a recycled PET charge, ground and washed, consisting of 20% by weight of opaque PET and comprising 5% by weight of pigment TiO 2 , and 12.9 kg / h of ethylene glycol (MEG), are worn at a temperature of 250 ° C. and then injected into a stirred reactor maintained at a pressure of 0.4 MPa. The residence time, defined as the ratio of the liquid volume of the reactor to the sum of the liquid volume flow rates entering the reactor, is fixed at 5 h. On leaving the reactor, the reaction effluent consists of 69.06% by weight of MEG, 27.74% by weight of BHET, 2.96% by weight of BHET dimer, and 0.24% by weight of TiO 2 .
    The ethylene glycol present in the reaction effluent is separated by evaporation in a succession of 4 flasks at temperatures ranging from 210 ° C to 130 ° C and pressures from 0.12 MPa to 0.001 MPa. At the end of this evaporation step, a flow of MEG of 11.1 kg / h and a liquid flow rich in BHET of 5.84 kg / h are recovered. The MEG stream consists almost exclusively of ethylene glycol and can therefore be recycled to the depolymerization reactor. The liquid stream rich in BHET consists of 80.50% by weight of BHET, 8.52% by weight of BHET dimer, 10.3% by weight of MEG and 0.68% by weight of TiO 2 .
    The liquid stream rich in BHET is then injected into a scraped film evaporator at a temperature of 220 ° C. and a pressure of 50 Pa. The residence time in the scraped film evaporator is 1 min. A gas effluent with a flow rate of 5.2 kg / h is recovered at the top of the scraped film evaporator. It consists of 88.5% by weight of BHET and 11.5% by weight of MEG and is free of any trace of TiO 2 . A heavy residue with a flow rate of 0.64 kg / h is recovered from the bottom of the scraped film evaporator and consists of 93.75% by weight of BHET oligomers and 6.25% by weight of TiO 2 .
    The gas effluent is condensed at 130 ° C to give a liquid stream of pre-purified BHET. The liquid flow of pre-purified BHET is compressed to 0.5 MPa and then feeds a fixed bed of activated carbon with an absorption capacity equal to 5% of its mass. At the end of this stage, a liquid stream of discolored and depigmented BHET is obtained, which is reinjected in a polymerization stage known to a person skilled in the art in order to produce virgin PET.
    EXAMPLE 2 - CONFORM
    This example illustrates the use of the process according to the invention with a 100% opaque PET filler.
    kg / h of flakes from a recycled PET charge, crushed and washed, consisting of 100% opaque PET, of which 5% by weight of TiO 2 pigment, and 12.9 kg / h of ethylene glycol (MEG), are worn at a temperature of 250 ° C. and then injected into a stirred reactor maintained at a pressure of 0.4 MPa. The residence time, defined as the ratio of the liquid volume of the reactor to the sum of the liquid volume flow rates entering the reactor, is fixed at 5 h. At the outlet of the reactor, the reaction effluent consists of 69.82% by weight of MEG, 26.63% by weight of BHET, 2.37% by weight of BHET dimer, and 1.18% by weight of TiO 2 .
    The ethylene glycol present in the reaction effluent is separated by evaporation in a succession of 4 flasks at temperatures ranging from 210 ° C to 130 ° C and pressures from 0.12 MPa to 0.001 MPa. At the end of this evaporation step, a flow of MEG of 11.2 kg / h and a liquid flow rich in BHET of 5.7 kg / h are recovered. The MEG stream consists almost exclusively of ethylene glycol and can therefore be recycled to the depolymerization reactor. The liquid stream rich in BHET consists of 78.9% by weight of BHET, 7.0% by weight of BHET dimer, 10.5% by weight of MEG and 3.51% by weight of TiO 2 .
    The liquid stream rich in BHET is then injected into a scraped film evaporator at a temperature of 220 ° C. and a pressure of 50 Pa. The residence time in the scraped film evaporator is 1 min. A gas effluent with a flow rate of 5.2 kg / h is recovered at the top of the scraped film evaporator. It consists of 88% by weight of BHET and 12% by weight of MEG and is free of any trace of TiO 2 . A heavy residue with a flow rate of 0.64 kg / h is recovered from the bottom of the scraped film evaporator and consists of 75% by weight of BHET oligomers and 25% by weight of TiO 2 .
    The gas effluent is condensed at 130 ° C to give a liquid stream of pre-purified BHET. The liquid flow of pre-purified BHET is compressed to 0.5 MPa and then feeds a fixed bed of activated carbon with an absorption capacity equal to 5% of its mass. At the end of this stage, a liquid stream of discolored and depigmented BHET is obtained, which is reinjected in a polymerization stage known to a person skilled in the art in order to produce virgin PET.
    EXAMPLE 3 - NON CONFORM
    This example illustrates the use of a process according to the prior art (JP3715812) with a filler comprising opaque PET.
    kg / h of flakes from a recycled PET charge, crushed and washed, consisting of 20% by weight of opaque PET and comprising 5% by weight of pigment TiO 2 , and 12.9 kg / h of ethylene glycol (MEG), are worn at a temperature of 250 ° C. and then injected into a stirred reactor maintained at a pressure of 0.4 MPa. The residence time, defined as the ratio of the liquid volume of the reactor to the sum of the liquid volume flow rates entering the reactor, is fixed at 5 h. On leaving the reactor, the reaction effluent consists of 69.06% by weight of MEG, 27.74% by weight of BHET, 2.96% by weight of BHET dimer, and 0.24% by weight of TiO 2 .
    Document JP3715812 teaches that it is necessary and important to carry out a prepurification, that is to say a filtration step (40-100 microns) followed by a deionization step, before the use of a separator. short contact time, this prepurification making it possible to extract from the flux the species promoting the repolymerization and coloring reactions of BHET.
    The depolymerization effluent is pumped and filtered at 100 ° C. and 0.4 MPa on a cartridge filter of 44 microns of porosity (325 mesh), then cooled to 50 ° C. and sent to a fixed bed containing an exchange resin. ions. The pressure is continuously monitored upstream of the filter and downstream of the resin bed. The pressure increases slowly in the first hours of operation and the pressure difference between the upstream of the filter and the downstream of the resin bed remains less than 2 bar, which preserves the integrity of the resin bed. After 12 hours of operation, the pressure increases sharply to 8 bar and the unit is stopped 30 minutes later due to blockage and loss of structure of the resin bed. The pressure difference between the upstream of the filter and the downstream of the resin bed is measured at 6 bar before capping.
    The sequences of stages of the prior art using a pre-purification by filtration and adsorption on resin therefore do not allow treatment with a filler containing opaque PET in an amount greater than 10% wt.
    权利要求:
    Claims (14)
    [1]
    1. A process for depolymerizing a polyester filler comprising opaque PET, said process comprising at least the following steps:
    a) a conditioning step supplied with said polyester filler;
    b) a depolymerization step by glycolysis fed at least by the effluent from step a) and by a make-up of diol, operated at a temperature between 200 and 400 ° C., with from 1 to 20 moles of diol per mole diester in said polyester filler and a residence time of the polyester of between 0.1 and 5 h;
    c) a step for separating the diol fed at least with the effluent from step b), operated at a temperature between 100 and 250 ° C., at a pressure lower than that of step b) and producing an effluent diol and an effluent rich in liquid monomers;
    d) a step for separating the effluent rich in liquid monomers from step c) into an effluent with heavy impurities and a pre-purified monomer effluent operated at a temperature below 250 ° C. and a pressure below 0.001 MPa with a liquid residence time of less than 10 min and
    e) a step of bleaching the pre-purified monomer effluent, carried out at a temperature between 100 and 250 ° C., and at a position between 0.1 and 1.0 MPa in the presence of an adsorbent and producing a purified monomer effluent.
    [2]
    2. The method of claim 1 wherein said polyester filler comprises at least 10% by weight of opaque PET.
    [3]
    3. Method according to one of the preceding claims in which step a) is carried out at a temperature between 225 and 275 ° C.
    [4]
    4. Method according to one of the preceding claims wherein said step a) comprises an extrusion section.
    [5]
    5. Method according to one of the preceding claims wherein said polyester filler is brought into contact with at least a fraction of the diol effluent from step c) in said step a).
    [6]
    6. Method according to one of the preceding claims wherein said step b) is carried out in the presence of a solid adsorbent.
    Ί. Method according to one of the preceding claims, in which said step b) is carried out in the presence of a heterogeneous catalyst comprising at least 50% by mass relative to the total mass of the catalyst of a solid solution consisting of at least one spinel of formula Z X AI 2 O ( 3 + X ) in which x is between 0 (limit excluded) and 1, and Z is chosen from Co, Fe, Mg, Mn, Ti, Zn, and comprising at most 50% mass d alumina and element Z oxide.
    [7]
    8. Method according to one of the preceding claims wherein said step c) is implemented in a succession of gas-liquid separations, the liquid effluent from the front section feeding the subsequent section, all of the gas effluents being condensed to form the diol effluent, the liquid effluent from the last gas-liquid separation section constituting the effluent rich in liquid monomers.
    [8]
    9. Method according to one of the preceding claims in which a fraction of the diol effluent from step c) is recycled to step b).
    [9]
    10. Method according to one of the preceding claims wherein said step d) is operated at a pressure less than 0.0005 MPa.
    [10]
    11. Method according to one of the preceding claims, in which said step d) is carried out with a liquid residence time of less than 1 min.
    [11]
    12. Method according to one of the preceding claims in which a fraction of said heavy impurities effluent is recycled to stage a) of conditioning and supply and / or to stage b) of depolymerization.
    [12]
    13. The method of claim 12 wherein a fraction of the diol effluent from step c) is mixed with the heavy impurities effluent from step d).
    [13]
    14. Method according to one of the preceding claims wherein said pre-purified monomer effluent from step d) is sent to a gas-liquid separation section, operated at a temperature between 100 and 250 ° C, and at a pressure between 0.00001 and 0.1 MPa.
    [14]
    15. Method according to one of the preceding claims in which the purified monomer effluent feeds a polymerization step in order to produce PET.
    类似技术:
    公开号 | 公开日 | 专利标题
    FR3053691A1|2018-01-12|PROCESS FOR DEPOLYMERIZING A POLYESTER COMPRISING OPAQUE POLYETHYLENE TEREPHTHALATE
    BE1018716A3|2011-07-05|CHEMICAL RECYCLING OF PLA BY HYDROLYSIS.
    BE1019608A3|2012-09-04|CHEMICAL RECYCLING OF PLA BY ALCOHOLISIS.
    SK283692B6|2003-12-02|The method of chemical recycling of polyethylene terephthalate waste
    WO2016096768A1|2016-06-23|Method for glycolysis of polyethylene terephthalate in two reaction steps
    WO2021122094A1|2021-06-24|Optimized method for depolymerizing a polyester comprising polyethylene terephthalate
    WO2021122095A1|2021-06-24|Improved method for depolymerizing a polyester comprising polyethylene terephthalate
    WO2021122096A1|2021-06-24|Method for obtaining a purified diester effluent by depolymerising a polyester comprising opaque polyethylene terephthalate
    WO2021140016A1|2021-07-15|Optimized depolymerization process by glycolysis of a polyester comprising polyethylene terephthalate
    EP3917641A1|2021-12-08|Method for producing a polyester terephthalate incorporating a depolymerization method
    WO2021140015A1|2021-07-15|Process for obtaining a purified diester monomer effluent by depolymerizing a polyester comprising colored and/or opaque and/or multilayered polyethylene terephthalate
    CA3125958A1|2020-08-06|Method for producing a terephthalate polyester from a monomeric mixture comprising a diester
    WO2021058923A2|2021-04-01|Process for joint recycling of composite items based on a thermoplastic polymer matrix
    JP2022519065A|2022-03-18|A method for producing a terephthalate polyester from a monomer mixture containing a diester.
    FR3080624A1|2019-11-01|ENHANCED ENERGY BALANCE COMPOSITE RECYCLING PROCESS
    同族专利:
    公开号 | 公开日
    JP6964101B2|2021-11-10|
    JP2019525980A|2019-09-12|
    FR3053691B1|2018-08-03|
    MX2018015436A|2019-04-11|
    US10544276B2|2020-01-28|
    US20190161595A1|2019-05-30|
    EP3481892A1|2019-05-15|
    CN109312101B|2021-12-14|
    KR20190026737A|2019-03-13|
    CA3029472A1|2018-01-11|
    CN109312101A|2019-02-05|
    BR112018076675A2|2019-04-02|
    WO2018007356A1|2018-01-11|
    引用文献:
    公开号 | 申请日 | 公开日 | 申请人 | 专利标题
    US3907868A|1974-02-15|1975-09-23|Du Pont|Polyester waste recovery|
    EP1130011A1|1999-09-09|2001-09-05|Aies Co., Ltd.|Process for removing titanium oxide or iron oxide red from depolymerization products obtained by glycolysis of polyesters containing titanium oxide or iron oxide red with ethylene glycol|
    US20040147624A1|2001-12-18|2004-07-29|Shuji Inada|Method of deionizing solution yielded by polyester decomposition with ethylene glycol|
    WO2016096767A1|2014-12-19|2016-06-23|IFP Energies Nouvelles|Method for glycolysis of polyethylene terephthalate in the presence of a heterogeneous catalyst|WO2020156965A1|2019-02-01|2020-08-06|IFP Energies Nouvelles|Method for producing a polyester terephthalate incorporating a depolymerization method|
    WO2020156966A1|2019-02-01|2020-08-06|IFP Energies Nouvelles|Method for producing a terephthalate polyester from a monomeric mixture comprising a diester|
    WO2021122094A1|2019-12-19|2021-06-24|IFP Energies Nouvelles|Optimized method for depolymerizing a polyester comprising polyethylene terephthalate|
    WO2021122095A1|2019-12-19|2021-06-24|IFP Energies Nouvelles|Improved method for depolymerizing a polyester comprising polyethylene terephthalate|
    WO2021122096A1|2019-12-19|2021-06-24|IFP Energies Nouvelles|Method for obtaining a purified diester effluent by depolymerising a polyester comprising opaque polyethylene terephthalate|
    WO2021140016A1|2020-01-09|2021-07-15|IFP Energies Nouvelles|Optimized depolymerization process by glycolysis of a polyester comprising polyethylene terephthalate|
    WO2021140015A1|2020-01-10|2021-07-15|IFP Energies Nouvelles|Process for obtaining a purified diester monomer effluent by depolymerizing a polyester comprising colored and/or opaque and/or multilayered polyethylene terephthalate|JPS4915255B1|1970-07-23|1974-04-13|
    US5635584A|1995-12-07|1997-06-03|Eastman Chemical Company|Process including glycolysis and subsequent purification for recycling polyester materials|
    JP3715812B2|1998-12-10|2005-11-16|株式会社アイエス|Chemical recycling method for polyethylene terephthalate waste|
    JP2003055300A|2001-08-17|2003-02-26|Is:Kk|METHOD FOR PRODUCING BIS-beta-HYDROXYETHYL TEREPHTHALATE|
    JP2004346229A|2003-05-23|2004-12-09|Is:Kk|Method for refining decomposition product solution obtained by decomposing polyester with ethylene glycol|
    JP2005330444A|2004-05-21|2005-12-02|Is:Kk|Method for recovering ester monomer from polyester fibers|
    JP5189266B2|2006-09-29|2013-04-24|株式会社ニスコ|Method for producing bis- terephthalate and method for producing polyethylene terephthalate|
    US9255194B2|2013-10-15|2016-02-09|International Business Machines Corporation|Methods and materials for depolymerizing polyesters|KR102223614B1|2019-06-12|2021-03-05|한국화학연구원|Depolymerization of Polymer Including Ester Group by Polar Chemical Compounds|
    NL2023681B1|2019-08-21|2021-04-13|Ioniqa Tech B V|Method and reactor system for depolymerising a terephthalate-containing polymer into reusable raw material|
    EP3875523A1|2020-03-03|2021-09-08|UAB Neo Group|Processes for recycling polyethylene terephthalate|
    WO2021211505A1|2020-04-13|2021-10-21|Eastman Chemical Company|Chemical recycling of colored plastics mixtures|
    WO2021261939A1|2020-06-26|2021-12-30|한국화학연구원|Efficient depolymerization method of polymer comprising ester functional group, and purification method thereof|
    法律状态:
    2017-07-31| PLFP| Fee payment|Year of fee payment: 2 |
    2018-01-12| PLSC| Publication of the preliminary search report|Effective date: 20180112 |
    2018-07-25| PLFP| Fee payment|Year of fee payment: 3 |
    2019-07-25| PLFP| Fee payment|Year of fee payment: 4 |
    2020-07-28| PLFP| Fee payment|Year of fee payment: 5 |
    2021-07-26| PLFP| Fee payment|Year of fee payment: 6 |
    优先权:
    申请号 | 申请日 | 专利标题
    FR1656423|2016-07-05|
    FR1656423A|FR3053691B1|2016-07-05|2016-07-05|PROCESS FOR DEPOLYMERIZING A POLYESTER COMPRISING OPAQUE POLYETHYLENE TEREPHTHALATE|FR1656423A| FR3053691B1|2016-07-05|2016-07-05|PROCESS FOR DEPOLYMERIZING A POLYESTER COMPRISING OPAQUE POLYETHYLENE TEREPHTHALATE|
    EP17739523.3A| EP3481892A1|2016-07-05|2017-07-04|Method for the depolymerisation of a polyester comprising opaque polyethylene terephthalate|
    BR112018076675-5A| BR112018076675A2|2016-07-05|2017-07-04|depolymerization process of a polyester comprising opaque polyethylene terephthalate|
    CN201780041196.0A| CN109312101B|2016-07-05|2017-07-04|Process for depolymerizing polyesters comprising opaque polyethylene terephthalate|
    US16/315,240| US10544276B2|2016-07-05|2017-07-04|Process for the depolymerization of a polyester comprising opaque polyethylene terephthalate|
    MX2018015436A| MX2018015436A|2016-07-05|2017-07-04|Method for the depolymerisation of a polyester comprising opaque polyethylene terephthalate.|
    JP2018568871A| JP6964101B2|2016-07-05|2017-07-04|Depolymerization method of polyester containing opaque polyethylene terephthalate|
    CA3029472A| CA3029472A1|2016-07-05|2017-07-04|Method for the depolymerisation of a polyester comprising opaque polyethylene terephthalate|
    KR1020197000194A| KR20190026737A|2016-07-05|2017-07-04|Method for depolymerization of polyester comprising opaque polyethylene terephthalate|
    PCT/EP2017/066577| WO2018007356A1|2016-07-05|2017-07-04|Method for the depolymerisation of a polyester comprising opaque polyethylene terephthalate|
    [返回顶部]