The present application claims priority to Italian Patent Application No. 102023000003012 filed on Feb. 22, 2023, which application is incorporated herein by reference in its entirety.
The present invention relates to a method for the chemical recycling and purification of waste polyesters by glycolysis reaction.
More in particular, the present invention relates to a method for preparing a polymeric material consisting of polyethylene terephthalate recycled by means of chemical recycling technology by glycolysis and subsequent polymerization, so as to obtain a purified product with chemical-physical-mechanical features (high intrinsic viscosity and high molecular weight) equal to virgin plastic material.
The intermediate produced by the glycolysis process can be easily repolymerized in a conventional PET production plant since the final reaction step is the same.
Polyethylene terephthalate (PET) is one of the most commonly used plastics, identified by symbol “1” according to the Voluntary Plastic Container Coding System suggested by the Society of the Plastics Industry in 1988. It is especially used in the field of bottles for single-use beverages and in the production of fibres.
PET is a polyester produced from two main industrial processes, the first of which is from a di-acid, terephthalic acid (TPA), and a mono-ethylene glycol (MEG) diol with the intermediate bis 2-hydroxyethyl terephthalate monomer (BHET). The dual functionality of the starting raw materials allows, by condensation thereof, the formation of a polymer chain the final molecular weight of which determines the mechanical features thereof.
The management of the end-of-life of plastic products and in particular of PET and polyesters, is of fundamental importance so as to avoid generating waste which accumulates in landfills and increases the already alarming numbers of plastic pollution.
At the same time, however, in the plastic polymers market, the demand for other polyesters with quality features such as to allow the use thereof in any field, such as the food field (not only for the production of bottles, but also containers with coupled materials), in the automotive field, in the pharmaceutical field continuously increases, as well as the need for such materials to be recycled and increasingly more performing.
In such a sense, plastic waste can actually be a resource if inserted in a circular recovery system for producing new plastic raw materials or for generating energy if recycling is not possible.
To date, the possible scenarios for managing the end-of-life of plastic are: mechanical recycling, chemical recycling, and energy recovery.
Recycling in general is the process which best allows achieving the “End Of Waste” purpose, i.e., the moment when the waste, subjected to specific treatment, ceases to be such, taking qualitative features such that it can be qualified as a new product.
However, the current plastic waste recycling technologies are essentially based on mechanical recycling. In such a process, after being collected and sorted into “homogeneous” polymer families, the waste is extruded and then reused without modifying the polymer structure.
However, the variety of waste collected leads to granules with additives of various origins which then make it impossible to obtain products which are qualitatively similar to the initial ones. The degradation effect given by the reprocessing temperature also depletes the properties of the polymer. Therefore, mechanically recycled plastics are actually used for a final product which is different from the one from which they were originally recovered, i.e., a product which is often of lower “value”.
Chemical recycling instead represents a possible and attractive solution by virtue of the possibility of generating a new polymer which can also be reused for applications with high quality requirements (e.g., food contact). In fact, chemical recycling allows the production of new raw materials, chemically modifying the chemical structure of the post-consumer polymer and obtaining a purified product.
The main chemical recycling technologies of polyesters and PET are based on chemical depolymerisation processes by solvolysis (glycolysis, methanolysis and hydrolysis) and pyrolysis, then depolymerisation and conversion processes. The former include the return to basic and intermediate monomers, decomposing the polymer by means of chemical reactions, which intermediates are then reused to obtain new virgin polymers. The second use high temperatures and gasification for producing hydrocarbon fractions.
With regard to the depolymerisation processes by solvolysis, there is still a need to provide a method which is capable of producing final intermediates and polyesters of high purity, limiting waste as much as possible and operating in an ecologically sustainable and economic manner.
In this context, it is the technical task underlying the present invention to provide a polymeric material recycled at a high technological level which allows achieving several joint objectives: recycling polyethylene terephthalate-based plastic materials regardless of the family of origin, the supply chain and the degree of purity of the plastic waste in input, thus reducing the amounts of plastic in the environment; reducing the use of fossil resources and reducing CO2 emissions, thus meeting increasingly stringent environmental needs; overcoming the limits of mechanical recycling with a competitive process with respect to other chemical recycling technologies and with a lower product cost with respect to the starting virgin material.
The technical task and object outlined above are substantially achieved by a method comprising the technical features set out in one or more of the appended claims, the definitions of which form an integral part of the present description.
Therefore, an object of the present invention is a method for preparing a polymeric material comprising or consisting of the steps of:
A further object of the present invention is a pilot industrial plant for studying and scaling-up the process as outlined above, comprising or consisting of:
A further object of the present invention is an industrial plant for carrying out the above process, the plant comprising or consisting of:
The present invention is inspired by the fact that chemical recycling allows overcoming the limits of the aforementioned mechanical processes, since:
Therefore, glycolysis is preferable as it is faster, more efficient and less expensive in terms of energy and waste, since by using glycol recoverable by distillation and leading to the production of the BHET monomer intermediate, it allows avoiding a process step by passing directly to the polymerisation step.
Further features and advantages of the present invention will become more apparent from the indicative and thus non-limiting description of a preferred, but not exclusive embodiment of the invention.
Therefore, a first object of the present invention is a method for preparing a polymeric material comprising or consisting of the steps of:
The raw material of polyethylene terephthalate (PET) can comprise or consist of post-consumer light, coloured, “light blue”, opaque bottles, post-consumer multilayer items with layers of PET coupled with barrier polymers for gas or metallic or polyolefins, printed PET layers, PET fibres or films, such as fabrics or polyester terephthalates, such as poly-trimethylene terephthalate, or polybutylene terephthalate, of any form and type available from the collection of wastes or from industrial production wastes.
In certain preferred embodiments, step a) comprises or consists of the following step:
More in detail, the raw material based on polyester terephthalates, in particular post-consumer PET, mostly PET stored preferably in the form of compressed bales, is conveyed on an “unpacker” for the removal of the wires containing iron and plastic. Once separated from said materials, the raw material based on polyester terephthalate is transported by conveyor belts to a rotating sieve of the “trommel” type for the elimination of coarse materials. The material then passes through a coarse metal removal system, in particular an “eddy current” metal detector, and is then conveyed to a label removal and pre-washing section from which it is transported at a further ferromagnetic metal removal system (e.g., magnetic metal detector).
The material thus processed is sent by conveyor belts to one or more cutting mills, through which the mincing into flakes occurs, which, by means of an auger, are conveyed to a water or salt water or slightly alkaline flotation tank, in which the heavier polyester fraction is separated by density from the fraction of lighter plastic impurities. The separated polyester fraction is sent to the drying and desiccation step for the elimination of all traces of water, to a fine foreign material separator and to a further “eddy current” metal detector for the further removal of fine metal impurities. Finally, preferably, the material thus obtained is separated by colour through an optical wavelength reader so as to separate the coloured flakes, preferably of any colour, from the colourless and transparent flakes.
In certain preferred embodiments, step b) comprises or consists of the following steps:
In step b1), preferably, the pre-treated material in step a) and excess ethylene glycol (mono ethylene glycol, MEG) are loaded in a stirred reactor and such a mixture is heated to obtain the reagent paste for subsequent depolymerisation.
Preferably, such a preparation is carried out under the following conditions:
Step b2) includes the transesterification of the polyester PET in the presence of an excess of MEG (molar ratio MEG/PET as defined above between 8:1 and 2:1, or about 4:1) and in the presence of a glycolysis catalyst, preferably selected from sodium carbonate, zinc chloride or zinc acetate, preferably with a continuous nitrogen flow to obtain the BHET recovery.
Preferably, the reaction is carried out in a tubular reactor called Oscillating Plug Flow Reactor (OPFR), capable of allowing high performance both in terms of product quality and in terms of process sustainability with regard to time and thus energy consumption.
The reaction of step b2) can be described by the following diagram:
Preferably, the reaction is carried out under the following conditions:
Therefore, the reaction of step b2) leads to the decomposition of the polyester by reversing the polymerisation reaction with the formation of a mixture of ethylene glycol, the BHET monomer intermediate and low molecular weight oligomers.
The conversion product is then mechanically filtered by a mesh filter to remove any unreacted physical impurities.
In certain preferred embodiments, step c) comprises or consists of the following steps:
In step c1) the resins used are, respectively, cation exchange, anion exchange and of decolourising adsorbent type for the removal, respectively, of metal ions, anions, and pigments/colourings of the plastic. The resins are packed inside heated columns, in which packed columns the fluid glycolysis product is passed for the time necessary for the adsorption of contaminants.
Once exhausted, the resins are regenerated by counter-current hot washes with ethylene glycol and/or other washing solutions such as solutions of soda, hydrochloric acid and/or sulfuric acid, or acetone.
In embodiments, the resins are selected from:
Preferably step c1) is carried out under the following conditions:
In step c2) the pigments/colourings removed by the adsorbent resin are recovered through solvent washing and distillation. Washing the exhausted resin with an appropriate solvent removes the colour adsorbed thereon, bringing it into solution. The coloured solution is conveyed to the distillation column where the solvent is separated from the pigments which are thus recovered and reusable.
Preferably step c2) is carried out under the following conditions:
In step c3) the product is subjected to increasing temperatures and decreasing vacuum in two reactors in series: respectively an evaporation reactor and a concentration reactor so as to eliminate more than 90% of the ethylene glycol, which, after being distilled and condensed through the stripping column, is optionally sent to one or more storage tanks to be able to then be reused in the process itself. A recovery of the BHET and oligomers is obtained with a yield between 80 and 99%.
Preferably step c3) is carried out under the following conditions:
The purified BHET can be stored molten, at a temperature between 120° C. and 180° C. in one or more tanks which will feed the polycondensation section.
In certain embodiments, the BHET obtainable with the methods of steps a), b) and c3) has the features shown in the following table 1.
In certain preferred embodiments, step d) comprises or consists of the following steps:
Step d1) is preferably carried out in the presence of the catalyst in weight percentage of about 0.025%-0.035%, or about 0.030% and of the stabiliser in weight percentage between 0.0025% and 0.0035%, or about 0.0030%.
The catalyst is preferably antimony oxide (Sb2O3), but also titanium oxide (TiO2), while the stabiliser is preferably phosphoric acid (H3PO4).
Other catalysts which can be used are, for example, metal acetates or carboxylates of zinc, magnesium, manganese or cobalt, or compounds with elements of the Fourth Group such as oxides or sulphides.
Other usable stabilisers are for example phosphoric acid esters such as tri-phenyl phosphites and tri-phenyl phosphates.
The section of the polycondensation step consists of the above-mentioned OPFR reactors divided into blocks of one to three or more OPFR reactors. The molten intermediate is preferably fed from a tank. The reaction occurs under vacuum, with different and increasing residual pressures and increasing temperatures in each reactor, so as to ensure a high efficiency of the process in terms of yields, product quality and consumption.
Furthermore, the ethylene glycol contained in the vapours generated during the reaction step is recovered after being conveyed to a stripping column with a thermal gradient of about 80° C. (180° C. at the bottom and 100° C. at the top): ethylene glycol is recovered at the bottom with a degree of purity such that it can be reused in the process, while volatile substances remain at the top.
Preferably, step d1) is carried out with ethylene glycol distillation under the following conditions:
The reaction is deemed concluded at a degree of intrinsic viscosity (IV) of 0.60-0.74 (measured according to the ISO 1628-5 or ASTM D 4603 standard) and a Molecular Weight MW (weight average molecular weight) of about 20000-30000.
A reaction diagram of step d1) according to a particular form of reaction is shown below:
In step d2), the pelletisation of the amorphous PET is carried out in a granulation plant which exploits an underwater cutting system. The molten polymer is pushed by a high-pressure pump through holes in a die, at the exit of which it is cut by a series of rotating blades, inside a chamber submerged in a high-speed water flow, which acts as a transport vehicle. The pellets have a size of about 3 mm×3 mm.
The pellets then undergo a nitrogen flow crystallisation reaction to bring the amorphous PET above the glass transition temperature (Tg) thereof in the crystallisation/finishing plant. The material is conveyed into a first hopper, heated by hot nitrogen at a temperature between 190° C. and 240° C., from which the material is sent by pneumatic transport to a second heating step at a lower temperature, between 170° C. and 220° C.
The heated polymer undergoes stretching and orientation processes and the polymer chains are rearranged in parallel, becoming tightly packed. Therefore, the crystallisation process consists of nucleation and spherulitic crystallisation.
Preferably, the crystallisation step is carried out under the following conditions:
The reaction is considered concluded at a Molecular Weight (weight average molecular weight, MW)>33000 resulting in an intrinsic viscosity value between 0.7-0.9 (measured according to ISO 1628-5 or ASTM D 4603 standard) and a crystallinity percentage greater than or equal to 40%.
Therefore, in certain embodiments, the polymeric material obtainable with the method described above has the features shown in the following table 2.
A second object of the present invention is a pilot industrial plant for studying and scaling-up the process as outlined above, comprising or consisting of the following operational units:
In certain embodiments, the operational units i) and ii) (reactors, column, purification systems) are managed through a computerised system (PLC), while the extrusion and pelletisation system of the operational unit iii) is managed by a specific computerised system.
The reactors are connected to each other and to the purification and granulation system by means of heated and insulated tubes.
In preferred embodiments, the operational unit i) comprises or consists of the following equipment:
In other embodiments the operational unit i) includes or is made up of the following equipment:
The operational unit ii) comprises or consists of the following equipment:
An exemplary diagram of the equipment from ii1-ii3 of the purification step of the pilot plant is shown in
The operational unit iii) comprises or consists of the following equipment:
An exemplary diagram of the extrusion and pelletisation system consisting of the equipment iii1-iii2 is shown in
According to the preferred embodiment, as shown in
Steps b1) and b2) are carried out as follows: the raw materials (flakes of polyester, ethylene glycol and catalyst, load RM) are loaded into the first stirred reactor CSTR A, heated to about 150-170° C. to promote the dissolution of the flakes in ethylene glycol. When the mass is completely melted, the paste is transferred to the OPFR tubular reactor where the glycolysis reaction occurs (step b2). The reacted mass is collected in the second stirred reactor CSTR B connected to the distillation column C (column-condenser-collection system) of the distillates to always ensure the excess of glycol for the complete conversion of the PET into BHET. In a completely analogous manner, in other embodiments, the raw materials can be loaded into the second stirred reactor CSTR B and the reacted mass can be collected in the first stirred reactor CSTR A which will be connected to the distillation column C (see for example
Step c3) is carried out as follows: in the second stirred reactor CSTR B in which the purified product is conveyed from the system of the operational unit ii) (see below), the excess ethylene glycol is removed by distillation and recovered through the stripping column connected to the condenser and the condensate collection system.
Step d1) is carried out as follows: the product obtained from step c3) which is in one of the two stirred reactors is added with the catalysts and the stabiliser, brought to the reaction temperature and transferred to the tubular reactor.
During the reaction, by the action of vacuum, ethylene glycol and volatile impurities are removed from the system by the column, condensed and collected in the condensate collector.
The purification and decolourisation of steps c1) and c2) is carried out by means of the equipment ii1-ii3.
In the resins packed inside the heated columns, the fluid glycolysis product is passed, cooled to the temperature of use of the resins by virtue of the heat exchangers, for the time necessary for the adsorption of the contaminants. Once exhausted, the resins are regenerated by counter-current hot washes with ethylene-glycol and/or other washing solutions such as solutions of soda, hydrochloric acid and/or sulfuric acid, or acetone.
Preferred examples of cationic resins are cationic resins of polystyrene matrix crosslinked with sulfonic acid functional groups in Na+ or H+ ionic form.
Preferred examples of anionic resins are anionic resins with styrene matrix with quaternary ammonium functional groups in Cl− ionic form.
Preferred examples of adsorbent resins are adsorbent resins with styrene matrix without functional groups.
As shown in
Step d2) is carried out as follows: once the polycondensation reaction has been completed, the molten polymer is transferred to the granulation step by means of nitrogen pressure through a tube maintained at about 260-270° C. and an outlet die with a variable diameter between 2 and 4 mm (equipment E).
The exit of the polymer occurs in the tank-cutter system (equipment T) in water heated to a temperature greater than that of the Tg of the polyester to avoid the vitrification of the molten product. A cooled polymer filament is formed which, through a system of metal guide arms in water, is conveyed to the cutting point where the pellet with dimensions of approximately 3 mm×3 mm is produced.
The polyester granule could need to be crystallised: for the crystallisation step in the pilot plant, a rotary evaporator R is used, which heats the granule to a certain temperature below 240° C., under vacuum or in a nitrogen stream.
Therefore, the polymeric material obtainable with the pilot plant described above has the features shown in Table 2.
In another embodiment, as shown in
Phases b1) and b2) are carried out as follows: the raw materials (polyester flakes, ethylene glycol and catalyst, load RM) are loaded into the third stirred reactor CSTR C, heated to approximately 150-170° C. to favor the dissolution of the flakes in the ethylene glycol. When the mass is completely melted, the paste is transferred to the OPFR tubular reactor where the glycolysis reaction takes place (phase b2). The reacted mass is collected in the same CSTR stirred reactor C connected to the distillate condenser-collector system to always guarantee the excess glycol for the complete conversion of PET into BHET.
Step c3) is carried out as follows: in the CSTR stirred reactor B where the purified product from the operating unit system ii) is conveyed (see below) the excess ethylene glycol is removed by distillation and recovered through the rectification column connected to the condenser and the condensate collection system.
Step d1) is carried out as follows: the product obtained from phase c3) which is found in the CSTR stirred reactor B, into which the purified product from the CSTR C reactor is conveyed, is added with the catalysts and the stabilizer, brought to the reaction temperature and transferred to the tubular reactor.
During the reaction, by the action of the vacuum, ethylene glycol and volatile impurities are removed from the system through the column, condensed and collected in the condensate collector.
The purification and decolourization of phases c1) and c2) is carried out using equipment ii1-ii3.
The fluid glycolysis product, coming from the third CSTR reactor C cooled to the temperature at which the resins are used thanks to the exchangers, is passed through the resins packed inside the heated columns for the time necessary for the adsorption of the contaminants. Once exhausted, the resins are regenerated by hot countercurrent washing with ethylene glycol and/or other washing solutions such as for example soda solutions, hydrochloric and/or sulfuric acid, or acetone.
As shown in
Step d2) is carried out as follows: once the polycondensation reaction is completed, the molten polymer is transferred to the granulation phase by means of nitrogen pressure via a pipe maintained at approximately 260-270° C. and an exit die with a diameter varying between 2 and 4 mm (equipment E).
The exit of the polymer occurs in the tank-cutter system (equipment T) in water heated to a temperature higher than that of the Tg of the polyester to avoid vitrification of the melt. A cooled polymer filament is formed which, through a system of metal guide arms in water, is conveyed to the cutting point where the pellet with dimensions of approximately 3 mm×3 mm is produced.
The polyester granule may need to be crystallized: for the crystallization phase in the pilot plant a rotary evaporator R is used, which heats the granule to a certain temperature below 240° C., under vacuum or in a stream of nitrogen.
Steps c1), c2) and d2) are performed as previously described in relation to the first embodiment.
The polymeric material obtainable with the pilot plant described above, therefore, has the characteristics shown in Table 2.
A still further object of the present invention is an industrial plant for carrying out the above process, the plant comprising or consisting of the following operational units:
In a particular embodiment, the operational unit A comprises or consists of the equipment described as follows:
A summary diagram of the operations which can be carried out with the operational units A1-A21 is shown in
The pre-treatment and preparation of the flakes according to step a) of the present invention is carried out by means of the equipment A1-A21.
A block diagram of the industrial plant comprising the operational units B to F is shown in
In a particular embodiment, the reactors B are of two different types, with different construction and operating principles and comprise or consist of:
A diagram of the OPFR reactor is shown in
The reactions of steps b1) and b2) are carried out by means of the reactors of operational unit B.
In a particular embodiment, the operational unit C comprises or consists of:
A diagram of the operational units consisting of the equipment C1) to C3) is shown in
The purification and decolourisation of steps c1) to c2) of the method of the invention is carried out by means of operational units C1-C3.
In a particular embodiment, the operational unit D comprises or consists of:
A diagram of a reactor D1 or D2 and column D3 are shown in
The evaporation and concentration steps of step c3) of the method of the invention are carried out by means of the operational units D1-D3.
In a particular embodiment, the operational units F are of the same type as the operational unit C2 and, in a particular embodiment of the invention, comprise or consist of:
The reactions of step d1) of the method of the invention are carried out by means of the operational unit F1.
The operational unit G consists of the submerged extrusion and pelletisation system for making the polyester pellets produced in step d1) and of the crystallisation and finishing system of the final product. In a particular embodiment, the operational unit G comprises or consists of:
An exemplary diagram of the operations implemented with the operational units G1-G12 is shown in
The pelletisation and crystallisation of step d2) is carried out by means of the operational units G1-G12.
The following operating parameters are used in operations 1 to 6:
The OPFR reactor is operated with a piston speed of 113 mm/min and a pressure of 3 bar FV.
In the order indicated by the arrows starting from the block in the upper left:
In the order indicated by the arrows starting from the block in the upper left: Polycondensation amorphous molten PET: IV max 0.75, crystallinity about 20%
The advantages of the present method and the plant for the implementation thereof are evident from the above.
In fact, although the glycolysis of PET is in itself a known process, the method of the invention stands out in that it allows improving the final features of the PET produced and the recovery of the materials used or present in the waste plastic material used (including coloured pigments).
Therefore, the technological innovation represented is evident in the fact that the process allows recovering a waste practically in the entirety thereof, avoiding excessive pre-treatments, with the aim of using it without distinction in terms of colour, form, and type by virtue of the purification technologies of the invention.
The polyester PET thus obtained is a new pure raw material identical to the virgin production material, produced with a process developed in several steps all within a single industrial plant and which can be marketed as such or mixed with any other plastic components.
It is apparent that only some particular embodiments of the present invention have been described, to which those skilled in the art will be able to make all changes required to adapt it to particular applications, without departing from the scope of protection of the present invention.
| Number | Date | Country | Kind |
|---|---|---|---|
| 102023000003012 | Feb 2023 | IT | national |