Process and composition for chemical recycling of polymers having reduced chlorine content

Abstract

A process for chemical recycling, wherein the process involves the steps of:i. supplying a composition of polymers;ii. subjecting the composition of polymers to a thermal treatment to obtain a pyrolysis oil;iii. optionally, subjecting the product obtained in step ii. to a hydrotreatment process;iv. subjecting the product obtained in step ii., or, when applied, the product obtained in step iii. to a thermal decomposition process, to obtain a chemical composition including ethylene and propylene;wherein the composition of polymers includes at most 10 ppm by weight of chlorine atoms, with regard to the total weight of the composition of polymers;wherein the composition of polymers includes polyolefin materials including one or more stabilisation compound(s), wherein the stabilisation compound(s) are selected from non-chlorine containing benzotriazole compounds, non-chlorine containing triazine compounds, and non-chlorine containing hydroxyl benzophenone compounds.

Description

CROSS REFERENCE TO RELATED APPLICATIONSThis application is a National Stage Application of PCT / EP2023 / 080980, filed Nov. 7, 2023, which claims the benefit of European Application No. 22209987.1, filed Nov. 28, 2022, both of which are incorporated by reference in their entirety herein.BACKGROUNDThe present invention relates to a process for chemical recycling of polymers. The invention further relates to a composition of polymers that is suitable for use in chemical recycling processes, in particular in chemical recycling processes involving pyrolysis of polymer compositions to obtain pyrolysis oils and subsequent processing of such pyrolysis oils via steam cracking or via refinery operations to obtain chemical feed streams for the production of polymers.In order to mitigate the end-of-life issues that relate to polymer materials, such as thermoplastics, there is as increasingly stringent drive to seek to for applications wherein polymer materials that are no longer considered to be of use for their original purpose can be utilised in a meaningful way, while minimising the burden on the environment, such as by discarding the materials as landfill or incineration.To achieve such, a vast array of recycling solutions for materials has been and is being investigated. As part of such investigations, a particular aspect that is paramount to be considered is the chemical composition of the polymer materials that one has available for processing. Typically, streams of polymer materials that one can access contain a wide variety of polymers of different chemical constitution, due to the fact that such streams are typically collected in a combined way; at the user level, e.g. the household, the knowledge and means that would allow the user to separate one type of polymer from the other generally is not available, nor can likely be expected to be available. And whilst there are certain plastics sorting technologies available, and increasingly developed, at present there remains the situation that the vast majority of waste plastics streams de facto are comprising polymer materials of differing chemical nature—and it is not foreseeable that this is likely to change.

[0005] Accordingly, it is appreciated that compositions of waste polymers of varying chemical nature can be processed via routes of desirably high value and desirably low environmental impact.

[0006] A particular route via which mixed streams of waste polymers can be processed that is gaining traction is via chemical recycling routes. Such routes typically involve a first stage of processing waste polymer streams of certain, defined, composition to produce one or more chemical compositions of oily nature, for example compositions that would be comparable to naphtha-type compositions as one can obtain from refining fossil crude oils, which stage then may be followed by the processing of such oily compositions via thermochemical decomposition processes to obtain hydrocarbon chemical compositions comprising a slate of chemicals that can be used again for manufacturing new, or ‘virgin’, products, including ‘virgin’ polymer materials such as for example polyethylenes and polypropylenes.

[0007] Such chemical recycling routes can be considered as a (part of) a solution for dealing with the abundantly available waste plastics streams. However, the composition of the waste plastics streams can affect the efficiency of the operation of such chemical recycling routes.

[0008] A particular element that may be detrimental to the capability of processing waste plastics via chemical recycling routes is chlorine. The presence of chlorine may lead to corrosion of equipment that is employed in unit operations for production of chemical compositions comprising ethylene and propylene, such as in steam cracking operations.

[0009] To mitigate this issue, processes of the art provide for separate unit operations to capture chlorine-containing compounds at various stages of the chemical recycling process. Such stages may include hydrotreatment stages, and polishing stages. As will be understood, in view of process efficiency it is preferred to minimise additional stages that need to be used in such chemical recycling process; each stage comes at a cost, involves additional consumption of energy, and leads to reduction of the yield of the process. Therefore, it is desired to employ a process in which the least amount of unit operations or process stages have to be incorporated.SUMMARY

[0010] The inventors of the present application have now found a particularly suitable process for chemical recycling, wherein the process involves the steps of:

[0011] i. supplying a composition of polymers;

[0012] ii. subjecting the composition of polymers to a thermal treatment to obtain a pyrolysis oil;

[0013] iii. optionally, subjecting the product obtained in step ii. to a hydrotreatment process;

[0014] iv. subjecting the product obtained in step ii., or, when applied, the product obtained in step iii. to a thermal decomposition process, to obtain a chemical composition comprising ethylene and propylene;

[0015] wherein the composition of polymers comprises at most 10 ppm by weight of chlorine atoms, with regard to the total weight of the composition of polymers;

[0016] wherein the composition of polymers comprises polyolefin materials comprising one or more stabilisation compound(s), wherein the stabilisation compound(s) are selected from non-chlorine containing benzotriazole compounds, non-chlorine containing triazine compounds, and non-chlorine containing hydroxyl benzophenone compounds.DETAILED DESCRIPTION

[0017] Such process allows for efficient chemical recycling of polymers, using a simplified process, wherein the corrosion of the equipment employed in the process is reduced. For example in operations wherein the chemical recycling involves steam cracking, such process allows for the use of an increased fraction of the product of step ii., e.g. a pyrolysis oil product, and / or the product of step iii, e.g. a hydrotreated pyrolysis oil product, without detrimental effects on the steam cracking process, such as corrosion, reduction of service life of the steam cracker, or fouling.

[0018] It is preferred that the stabilisation compound(s) are selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphenyl)-6-(2-hydroxy-4-octyloxyphenyl-1,3,5-triazine, 2-hydroxy-4-methoxy benzophenone, 2-hydroxy-4-n-octyloxy benzophenone, 2-hydroxy-4-n-dodecyloxy benzophenone, 2,4-dihydroxy benzophenone, 2-hydroxy-4-acryloxy benzophenone, 2-hydroxy-4-(benzyloxy) benzophenone, 2,2′-dihydroxy-4-methoxy benzophenone, 2,2′,4,4′-tetrahydroxy benzophenone, 2,2′-dihydroxy-4,4′-dimoethoxy benzophenone, 2-hydroxy-4-allyloxy benzophenone, 2-hydroxy-4-(2-hydroxyethoxy) benzophenone, and 1,4-bis(4-benzoyl-3-hydroxyphenoxy) butane.

[0019] For example, the composition of polymer may comprise ≤5000 ppm by weight of the stabilisation compound(s), preferably ≥500 and ≤5000 ppm, more preferably ≥500 and ≤3000 ppm, with regard to the total weight of the composition of polymers.

[0020] Preferably, the composition of polymers comprises ≥1 ppb by weight of chlorine atoms, with regard to the total weight of the composition of polymers, preferably ≥5 ppb, more preferably ≥10 ppb.

[0021] Preferably, the composition of polymers comprises ≤5 ppm by weight of chlorine atoms.

[0022] The thermal treatment of step ii. may for example involve a low-severity pyrolysis process, wherein the pyrolysis of the composition of polymers is performed at a temperature of ≥250° C. and ≤450° C., or a high-severity pyrolysis process, wherein the pyrolysis of the composition of polymers is performed at a temperature of >450° C. and ≤650° C.

[0023] Alternatively, the thermal treatment may be a catalytic process, preferably wherein the thermal treatment is a process operated in the presence of a ZSM-5 zeolite catalyst and / or a spent FCC catalyst.

[0024] In the process of the present invention, the hydrotreatment step iii. may be performed at a temperature of ≤350° C., in the presence of hydrogen, preferably at a pressure of ≤10.0 MPa, preferably ≥1.0 and ≤10.0 MPa, more preferable at ≥2.0 and ≤7.0 MPa.

[0025] For example, the hydrotreatment step iii. may be performed in the presence of a catalyst, wherein the catalyst is selected from a cobalt-molybdenum catalyst on alumina support, a nickel-molybdenum catalyst on alumina support, a tungsten-molybdenum catalyst on alumina support, a platinum-palladium catalyst on alumina support, a nickel sulphide catalyst, a molybdenum sulphide catalyst, or a nickel-molybdenum sulphide catalyst.

[0026] The thermal decomposition process of step iv. may be a steam cracking process, preferably wherein the steam cracking occurs in a steam cracking unit comprising heated coils, wherein the coil outlet temperature (COT) is in the range of 800° C. to 870° C. Alternatively, the thermal decomposition process of step iv. may be a catalytic cracking process.

[0027] In the embodiment wherein the thermal decomposition process of step iv. is a steam cracking process, the feed composition that is supplied to the steam cracking process may for example comprise ≥2.5 wt% and ≤75.0 wt %, preferably ≥5.0 wt % and ≤50.0 wt %, more preferably ≥10.0 wt % and ≤50.0 wt % of the product obtained in step ii.

[0028] Alternatively, the feed composition that is supplied to the steam cracking process may for example comprise ≥2.5 wt % and ≤75.0 wt %, preferably ≥5.0 wt % and ≤50.0 wt %, more preferably ≥10.0 wt % and ≤50.0 wt % of the product obtained in step iii.In the Process of the Present Invention, the Composition of Polymers May for

[0029] example comprise:

[0030] ≥70.0 wt % of polyolefin compositions;

[0031] ≤20.0 wt % of polyesters compositions;

[0032] ≤20 wt % of polyamide compositions; and

[0033] ≤10 ppm by weight of chlorine atoms, preferably ≥1 ppb and ≤10 ppm, more preferably ≥10 ppb and ≤5 ppm; with regard to the total weight of the composition of polymers.

[0034] The invention also relates to a composition of polymers comprising:

[0035] ≥70.0 wt% of polyolefin compositions;

[0036] ≥0.1 and ≤20.0 wt % of polyester compositions;

[0037] ≥0.1 and ≤20 wt % of polyamide compositions; and

[0038] ≤10 ppm by weight of chlorine atoms, preferably ≥1 ppb and ≤10 ppm, more preferably ≥10 ppb and ≤5 ppm; with regard to the total weight of the composition of polymers.

[0039] The composition of polymers may for example comprise one or more stabilisation compound(s), wherein the stabilisation compound(s) are selected from non-chlorine containing benzotriazole compounds, non-chlorine containing triazine compounds, and non-chlorine containing hydroxyl benzophenone compounds.

[0040] The stabilisation compound(s) may for example be selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphenyl)-6-(2-hydroxy-4-octyloxyphenyl-1,3,5-triazine, 2-hydroxy-4-methoxy benzophenone, 2-hydroxy-4-n-octyloxy benzophenone, 2-hydroxy-4-n-dodecyloxy benzophenone, 2,4-dihydroxy benzophenone, 2-hydroxy-4-acryloxy benzophenone, 2-hydroxy-4-(benzyloxy) benzophenone, 2,2′-dihydroxy-4-methoxy benzophenone, 2,2′,4,4′-tetrahydroxy benzophenone, 2,2′-dihydroxy-4,4′-dimoethoxy benzophenone, 2-hydroxy-4-allyloxy benzophenone, 2-hydroxy-4-(2-hydroxyethoxy) benzophenone, and 1,4-bis(4-benzoyl-3-hydroxyphenoxy) butane.

[0041] It is particularly preferred that the composition of polymers is obtained as a waste plastics stream, for example from post-consumer or household wastes.

[0042] The invention also relates to the use of a composition of polymers according to the invention for the reduction of fouling and / or corrosion during steam cracking of chemical feeds comprising waste plastics-derived materials.

[0043] Such process allows for efficient chemical recycling of polymers, using a simplified process, wherein the corrosion of the equipment employed in the process is reduced.

[0044] The quantity of chlorine atoms in the composition of polymers may for example be determined in accordance with ASTM UOP 779-08.

[0045] The hydrotreatment process of step iii. may for example be performed in one of more vessel(s) configured to hold a hydrotreatment catalyst. The vessel may be configured to operate in gas phase, liquid phase, vapour-liquid phase, or slurry phase.

[0046] The vessel may include one or more beds of the hydrotreatment catalyst. Such bed(s) may be fixed bed(s), fluidized bed(s), moving bed(s), slurry bed(s), or combinations thereof. The vessel may be operated in adiabatic, isothermal, non-adiabatic, or non-isothermal conditions.

[0047] In the hydrotreatment step, the product of step ii. may be subjected to treatment in the presence of hydrogen, wherein the volume flow ratio of hydrogen to the product of step ii. may for example be 10 to 3000, preferably 200 to 1000.

[0048] The hydrotreatment step iii may be performed in the presence of a catalyst. Such catalyst may for example be a catalyst selected from a cobalt-molybdenum catalyst on alumina support, a nickel-molybdenum catalyst on alumina support, a tungsten-molybdenum catalyst on alumina support, a platinum-palladium catalyst on alumina support, a nickel sulphide catalyst, a molybdenum sulphide catalyst, or a nickel-molybdenum sulphide catalyst.

[0049] The catalyst that may be used in the hydrotreatment step iii. may for example be sulphided.

[0050] The composition of polymers preferably comprises ≥70.0 wt % of polyolefins. Such polyolefins preferably comprise polyethylenes and polypropylenes. In particular, the polyolefins may comprise ≥80.0 wt % of polyethylenes, or ≥90.0 wt % of polyethylenes. The polyolefins may comprise ≤20.0 wt % of polypropylenes, or ≤10.0 wt % of polypropylenes.

[0051] Such polyethylenes may be a composition comprising low-density polyethylenes, linear low-density polyethylenes, and high-density polyethylenes.

[0052] It is particularly preferred that the composition of polymers comprises a high fraction of polyolefins, such as ≥70.0 wt %, or ≥80.0 wt %, or ≥90.0 wt %, with regard to the total weight of the composition of polymers. Compositions of polymers comprising such high fraction of polyolefins are particularly suitable for chemical recycling via catalytic or non-catalytic thermal treatment processes, due to the fact that their polymer structure is based on linear monomers, which are suitable for thermal cracking.

[0053] Via such thermal cracking, for example steam cracking or catalytic cracking, the composition of plastics, in particular a composition of waste plastics, may be converted into chemical building blocks, in particular ethylene and propylene.

[0054] Accordingly, the process of the present invention allows for the suitable conversion of waste plastics into new plastics of high quality, thereby creating a circular economy of material use.

Examples

Embodiment Construction

[0017]Such process allows for efficient chemical recycling of polymers, using a simplified process, wherein the corrosion of the equipment employed in the process is reduced. For example in operations wherein the chemical recycling involves steam cracking, such process allows for the use of an increased fraction of the product of step ii., e.g. a pyrolysis oil product, and / or the product of step iii, e.g. a hydrotreated pyrolysis oil product, without detrimental effects on the steam cracking process, such as corrosion, reduction of service life of the steam cracker, or fouling.

[0018]It is preferred that the stabilisation compound(s) are selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphen...

CROSS REFERENCE TO RELATED APPLICATIONSThis application is a National Stage Application of PCT / EP2023 / 080980, filed Nov. 7, 2023, which claims the benefit of European Application No. 22209987.1, filed Nov. 28, 2022, both of which are incorporated by reference in their entirety herein.BACKGROUNDThe present invention relates to a process for chemical recycling of polymers. The invention further relates to a composition of polymers that is suitable for use in chemical recycling processes, in particular in chemical recycling processes involving pyrolysis of polymer compositions to obtain pyrolysis oils and subsequent processing of such pyrolysis oils via steam cracking or via refinery operations to obtain chemical feed streams for the production of polymers.In order to mitigate the end-of-life issues that relate to polymer materials, such as thermoplastics, there is as increasingly stringent drive to seek to for applications wherein polymer materials that are no longer considered to be of use for their original purpose can be utilised in a meaningful way, while minimising the burden on the environment, such as by discarding the materials as landfill or incineration.To achieve such, a vast array of recycling solutions for materials has been and is being investigated. As part of such investigations, a particular aspect that is paramount to be considered is the chemical composition of the polymer materials that one has available for processing. Typically, streams of polymer materials that one can access contain a wide variety of polymers of different chemical constitution, due to the fact that such streams are typically collected in a combined way; at the user level, e.g. the household, the knowledge and means that would allow the user to separate one type of polymer from the other generally is not available, nor can likely be expected to be available. And whilst there are certain plastics sorting technologies available, and increasingly developed, at present there remains the situation that the vast majority of waste plastics streams de facto are comprising polymer materials of differing chemical nature—and it is not foreseeable that this is likely to change.

[0005] Accordingly, it is appreciated that compositions of waste polymers of varying chemical nature can be processed via routes of desirably high value and desirably low environmental impact.

[0006] A particular route via which mixed streams of waste polymers can be processed that is gaining traction is via chemical recycling routes. Such routes typically involve a first stage of processing waste polymer streams of certain, defined, composition to produce one or more chemical compositions of oily nature, for example compositions that would be comparable to naphtha-type compositions as one can obtain from refining fossil crude oils, which stage then may be followed by the processing of such oily compositions via thermochemical decomposition processes to obtain hydrocarbon chemical compositions comprising a slate of chemicals that can be used again for manufacturing new, or ‘virgin’, products, including ‘virgin’ polymer materials such as for example polyethylenes and polypropylenes.

[0007] Such chemical recycling routes can be considered as a (part of) a solution for dealing with the abundantly available waste plastics streams. However, the composition of the waste plastics streams can affect the efficiency of the operation of such chemical recycling routes.

[0008] A particular element that may be detrimental to the capability of processing waste plastics via chemical recycling routes is chlorine. The presence of chlorine may lead to corrosion of equipment that is employed in unit operations for production of chemical compositions comprising ethylene and propylene, such as in steam cracking operations.

[0009] To mitigate this issue, processes of the art provide for separate unit operations to capture chlorine-containing compounds at various stages of the chemical recycling process. Such stages may include hydrotreatment stages, and polishing stages. As will be understood, in view of process efficiency it is preferred to minimise additional stages that need to be used in such chemical recycling process; each stage comes at a cost, involves additional consumption of energy, and leads to reduction of the yield of the process. Therefore, it is desired to employ a process in which the least amount of unit operations or process stages have to be incorporated.SUMMARY

[0010] The inventors of the present application have now found a particularly suitable process for chemical recycling, wherein the process involves the steps of:

[0011] i. supplying a composition of polymers;

[0012] ii. subjecting the composition of polymers to a thermal treatment to obtain a pyrolysis oil;

[0013] iii. optionally, subjecting the product obtained in step ii. to a hydrotreatment process;

[0014] iv. subjecting the product obtained in step ii., or, when applied, the product obtained in step iii. to a thermal decomposition process, to obtain a chemical composition comprising ethylene and propylene;

[0015] wherein the composition of polymers comprises at most 10 ppm by weight of chlorine atoms, with regard to the total weight of the composition of polymers;

[0016] wherein the composition of polymers comprises polyolefin materials comprising one or more stabilisation compound(s), wherein the stabilisation compound(s) are selected from non-chlorine containing benzotriazole compounds, non-chlorine containing triazine compounds, and non-chlorine containing hydroxyl benzophenone compounds.DETAILED DESCRIPTION

[0017] Such process allows for efficient chemical recycling of polymers, using a simplified process, wherein the corrosion of the equipment employed in the process is reduced. For example in operations wherein the chemical recycling involves steam cracking, such process allows for the use of an increased fraction of the product of step ii., e.g. a pyrolysis oil product, and / or the product of step iii, e.g. a hydrotreated pyrolysis oil product, without detrimental effects on the steam cracking process, such as corrosion, reduction of service life of the steam cracker, or fouling.

[0018] It is preferred that the stabilisation compound(s) are selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphenyl)-6-(2-hydroxy-4-octyloxyphenyl-1,3,5-triazine, 2-hydroxy-4-methoxy benzophenone, 2-hydroxy-4-n-octyloxy benzophenone, 2-hydroxy-4-n-dodecyloxy benzophenone, 2,4-dihydroxy benzophenone, 2-hydroxy-4-acryloxy benzophenone, 2-hydroxy-4-(benzyloxy) benzophenone, 2,2′-dihydroxy-4-methoxy benzophenone, 2,2′,4,4′-tetrahydroxy benzophenone, 2,2′-dihydroxy-4,4′-dimoethoxy benzophenone, 2-hydroxy-4-allyloxy benzophenone, 2-hydroxy-4-(2-hydroxyethoxy) benzophenone, and 1,4-bis(4-benzoyl-3-hydroxyphenoxy) butane.

[0019] For example, the composition of polymer may comprise ≤5000 ppm by weight of the stabilisation compound(s), preferably ≥500 and ≤5000 ppm, more preferably ≥500 and ≤3000 ppm, with regard to the total weight of the composition of polymers.

[0020] Preferably, the composition of polymers comprises ≥1 ppb by weight of chlorine atoms, with regard to the total weight of the composition of polymers, preferably ≥5 ppb, more preferably ≥10 ppb.

[0021] Preferably, the composition of polymers comprises ≤5 ppm by weight of chlorine atoms.

[0022] The thermal treatment of step ii. may for example involve a low-severity pyrolysis process, wherein the pyrolysis of the composition of polymers is performed at a temperature of ≥250° C. and ≤450° C., or a high-severity pyrolysis process, wherein the pyrolysis of the composition of polymers is performed at a temperature of >450° C. and ≤650° C.

[0023] Alternatively, the thermal treatment may be a catalytic process, preferably wherein the thermal treatment is a process operated in the presence of a ZSM-5 zeolite catalyst and / or a spent FCC catalyst.

[0024] In the process of the present invention, the hydrotreatment step iii. may be performed at a temperature of ≤350° C., in the presence of hydrogen, preferably at a pressure of ≤10.0 MPa, preferably ≥1.0 and ≤10.0 MPa, more preferable at ≥2.0 and ≤7.0 MPa.

[0025] For example, the hydrotreatment step iii. may be performed in the presence of a catalyst, wherein the catalyst is selected from a cobalt-molybdenum catalyst on alumina support, a nickel-molybdenum catalyst on alumina support, a tungsten-molybdenum catalyst on alumina support, a platinum-palladium catalyst on alumina support, a nickel sulphide catalyst, a molybdenum sulphide catalyst, or a nickel-molybdenum sulphide catalyst.

[0026] The thermal decomposition process of step iv. may be a steam cracking process, preferably wherein the steam cracking occurs in a steam cracking unit comprising heated coils, wherein the coil outlet temperature (COT) is in the range of 800° C. to 870° C. Alternatively, the thermal decomposition process of step iv. may be a catalytic cracking process.

[0027] In the embodiment wherein the thermal decomposition process of step iv. is a steam cracking process, the feed composition that is supplied to the steam cracking process may for example comprise ≥2.5 wt% and ≤75.0 wt %, preferably ≥5.0 wt % and ≤50.0 wt %, more preferably ≥10.0 wt % and ≤50.0 wt % of the product obtained in step ii.

[0028] Alternatively, the feed composition that is supplied to the steam cracking process may for example comprise ≥2.5 wt % and ≤75.0 wt %, preferably ≥5.0 wt % and ≤50.0 wt %, more preferably ≥10.0 wt % and ≤50.0 wt % of the product obtained in step iii.In the Process of the Present Invention, the Composition of Polymers May for

[0029] example comprise:

[0030] ≥70.0 wt % of polyolefin compositions;

[0031] ≤20.0 wt % of polyesters compositions;

[0032] ≤20 wt % of polyamide compositions; and

[0033] ≤10 ppm by weight of chlorine atoms, preferably ≥1 ppb and ≤10 ppm, more preferably ≥10 ppb and ≤5 ppm; with regard to the total weight of the composition of polymers.

[0034] The invention also relates to a composition of polymers comprising:

[0035] ≥70.0 wt% of polyolefin compositions;

[0036] ≥0.1 and ≤20.0 wt % of polyester compositions;

[0037] ≥0.1 and ≤20 wt % of polyamide compositions; and

[0038] ≤10 ppm by weight of chlorine atoms, preferably ≥1 ppb and ≤10 ppm, more preferably ≥10 ppb and ≤5 ppm; with regard to the total weight of the composition of polymers.

[0039] The composition of polymers may for example comprise one or more stabilisation compound(s), wherein the stabilisation compound(s) are selected from non-chlorine containing benzotriazole compounds, non-chlorine containing triazine compounds, and non-chlorine containing hydroxyl benzophenone compounds.

[0040] The stabilisation compound(s) may for example be selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphenyl)-6-(2-hydroxy-4-octyloxyphenyl-1,3,5-triazine, 2-hydroxy-4-methoxy benzophenone, 2-hydroxy-4-n-octyloxy benzophenone, 2-hydroxy-4-n-dodecyloxy benzophenone, 2,4-dihydroxy benzophenone, 2-hydroxy-4-acryloxy benzophenone, 2-hydroxy-4-(benzyloxy) benzophenone, 2,2′-dihydroxy-4-methoxy benzophenone, 2,2′,4,4′-tetrahydroxy benzophenone, 2,2′-dihydroxy-4,4′-dimoethoxy benzophenone, 2-hydroxy-4-allyloxy benzophenone, 2-hydroxy-4-(2-hydroxyethoxy) benzophenone, and 1,4-bis(4-benzoyl-3-hydroxyphenoxy) butane.

[0041] It is particularly preferred that the composition of polymers is obtained as a waste plastics stream, for example from post-consumer or household wastes.

[0042] The invention also relates to the use of a composition of polymers according to the invention for the reduction of fouling and / or corrosion during steam cracking of chemical feeds comprising waste plastics-derived materials.

[0043] Such process allows for efficient chemical recycling of polymers, using a simplified process, wherein the corrosion of the equipment employed in the process is reduced.

[0044] The quantity of chlorine atoms in the composition of polymers may for example be determined in accordance with ASTM UOP 779-08.

[0045] The hydrotreatment process of step iii. may for example be performed in one of more vessel(s) configured to hold a hydrotreatment catalyst. The vessel may be configured to operate in gas phase, liquid phase, vapour-liquid phase, or slurry phase.

[0046] The vessel may include one or more beds of the hydrotreatment catalyst. Such bed(s) may be fixed bed(s), fluidized bed(s), moving bed(s), slurry bed(s), or combinations thereof. The vessel may be operated in adiabatic, isothermal, non-adiabatic, or non-isothermal conditions.

[0047] In the hydrotreatment step, the product of step ii. may be subjected to treatment in the presence of hydrogen, wherein the volume flow ratio of hydrogen to the product of step ii. may for example be 10 to 3000, preferably 200 to 1000.

[0048] The hydrotreatment step iii may be performed in the presence of a catalyst. Such catalyst may for example be a catalyst selected from a cobalt-molybdenum catalyst on alumina support, a nickel-molybdenum catalyst on alumina support, a tungsten-molybdenum catalyst on alumina support, a platinum-palladium catalyst on alumina support, a nickel sulphide catalyst, a molybdenum sulphide catalyst, or a nickel-molybdenum sulphide catalyst.

[0049] The catalyst that may be used in the hydrotreatment step iii. may for example be sulphided.

[0050] The composition of polymers preferably comprises ≥70.0 wt % of polyolefins. Such polyolefins preferably comprise polyethylenes and polypropylenes. In particular, the polyolefins may comprise ≥80.0 wt % of polyethylenes, or ≥90.0 wt % of polyethylenes. The polyolefins may comprise ≤20.0 wt % of polypropylenes, or ≤10.0 wt % of polypropylenes.

[0051] Such polyethylenes may be a composition comprising low-density polyethylenes, linear low-density polyethylenes, and high-density polyethylenes.

[0052] It is particularly preferred that the composition of polymers comprises a high fraction of polyolefins, such as ≥70.0 wt %, or ≥80.0 wt %, or ≥90.0 wt %, with regard to the total weight of the composition of polymers. Compositions of polymers comprising such high fraction of polyolefins are particularly suitable for chemical recycling via catalytic or non-catalytic thermal treatment processes, due to the fact that their polymer structure is based on linear monomers, which are suitable for thermal cracking.

[0053] Via such thermal cracking, for example steam cracking or catalytic cracking, the composition of plastics, in particular a composition of waste plastics, may be converted into chemical building blocks, in particular ethylene and propylene.

[0054] Accordingly, the process of the present invention allows for the suitable conversion of waste plastics into new plastics of high quality, thereby creating a circular economy of material use.

Examples

Embodiment Construction

[0017]Such process allows for efficient chemical recycling of polymers, using a simplified process, wherein the corrosion of the equipment employed in the process is reduced. For example in operations wherein the chemical recycling involves steam cracking, such process allows for the use of an increased fraction of the product of step ii., e.g. a pyrolysis oil product, and / or the product of step iii, e.g. a hydrotreated pyrolysis oil product, without detrimental effects on the steam cracking process, such as corrosion, reduction of service life of the steam cracker, or fouling.

[0018]It is preferred that the stabilisation compound(s) are selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphen...

Claims

1. A process for chemical recycling of polymers, the process involving the steps of:i. supplying a composition of polymers;ii. subjecting the composition of polymers to a thermal treatment to obtain a pyrolysis oil;iii. optionally, subjecting the product obtained in step ii. to a hydrotreatment process;iv. subjecting the product obtained in step ii., or, when applied, the product obtained in step iii. to a thermal decomposition process, to obtain a chemical composition comprising ethylene and propylene;wherein the composition of polymers comprises at most 10 ppm by weight of chlorine atoms, with regard to the total weight of the composition of polymers;wherein the composition of polymers comprises polyolefin materials comprising one or more stabilisation compound(s), wherein the stabilisation compound(s) are selected from non-chlorine containing benzotriazole compounds, non-chlorine containing triazine compounds, and non-chlorine containing hydroxyl benzophenone compounds.

2. The process according to claim 1, wherein the stabilisation compound(s) are selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphenyl)-6-(2-hydroxy-4-octyloxyphenyl-1,3,5-triazine, 2-hydroxy-4-methoxy benzophenone, 2-hydroxy-4-n-octyloxy benzophenone, 2-hydroxy-4-n-dodecyloxy benzophenone, 2,4-dihydroxy benzophenone, 2-hydroxy-4-acryloxy benzophenone, 2-hydroxy-4-(benzyloxy) benzophenone, 2,2′-dihydroxy-4-methoxy benzophenone, 2,2′,4,4′-tetrahydroxy benzophenone, 2,2′-dihydroxy-4,4′-dimoethoxy benzophenone, 2-hydroxy-4-allyloxy benzophenone, 2-hydroxy-4-(2-hydroxyethoxy) benzophenone, and 1,4-bis(4-benzoyl-3-hydroxyphenoxy) butane.

3. The process according to claim 1, wherein the composition of polymers comprises ≥1 ppb by weight of chlorine atoms, with regard to the total weight of the composition of polymers.

4. The process according to claim 1, wherein the thermal treatment of step ii. involves a low-severity pyrolysis process, wherein the pyrolysis of the composition of polymers is performed at a temperature of ≥250° C. and ≤450° C., or a high-severity pyrolysis process, wherein the pyrolysis of the composition of polymers is performed at a temperature of >450° C. and ≤650° C..

5. The process according to claim 1, wherein the thermal treatment is a catalytic process.

6. The process according to claim 1, wherein the hydrotreatment step iii. is performed at a temperature of ≤350° C., in the presence of hydrogen.

7. The process according to claim 1, wherein the hydrotreatment step iii. is performed in the presence of a catalyst, wherein the catalyst is selected from a cobalt-molybdenum catalyst on alumina support, a nickel-molybdenum catalyst on alumina support, a tungsten-molybdenum catalyst on alumina support, a platinum-palladium catalyst on alumina support, a nickel sulphide catalyst, a molybdenum sulphide catalyst, or a nickel-molybdenum sulphide catalyst.

8. The process according to claim 1, wherein the thermal decomposition process of step iv. is a steam cracking process; or wherein the thermal decomposition process of step iv. is a catalytic cracking process.

9. The process according to claim 8, wherein the feed composition that is supplied to the steam cracking process comprises ≥2.5 wt % and ≤75.0 wt % of the product obtained in step ii;and / orwherein the feed composition that is supplied to the steam cracking process comprises ≥2.5 wt % and ≤75.0 wt %; of the product obtained in step iii.

10. The process according to claim 1, wherein the composition of polymers comprises:≥70.0 wt % of polyolefin compositions;≤20.0 wt % of polyesters compositions;≤20 wt % of polyamide compositions; and≤10 ppm by weight of chlorine atoms;with regard to the total weight of the composition of polymers.

11. A composition of polymers comprising:≥70.0 wt % of polyolefin compositions;>0.1 and ≤20.0 wt % of polyester compositions;≥0.1 and ≤20 wt % of polyamide compositions; and≤10 ppm by weight of chlorine atoms;with regard to the total weight of the composition of polymers.

12. The composition according to claim 11, wherein the composition of polymers comprises one or more stabilisation compound(s), wherein the stabilisation compound(s) are selected from non-chlorine containing benzotriazole compounds, non-chlorine containing triazine compounds and non-chlorine containing hydroxyl benzophenone compounds.

13. The composition according to claim 12, wherein the stabilisation compound(s) are selected from 2-(2′-hydroxy-3′-5′-di-t-butylphenyl)-benzotriazole, 2-(2′-hydroxy-3′-5′-t-amylphenyl)benzotriazole, 2-(2′-hydroxy-5′-methylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-butylphenyl)benzotriazole, 2-(2′-hydroxy-5′-t-octylphenyl)benzotriazole, 1,6-hexanediol bis(benzotriazol-2-yl-5-t-butyl-4-hydroxybenzenepropionate), 2,4-bis(2,4-dimethylphenyl)-6-(2-hydroxy-4-octyloxyphenyl-1,3,5-triazine, 2-hydroxy-4-methoxy benzophenone, 2-hydroxy-4-n-octyloxy benzophenone, 2-hydroxy-4-n-dodecyloxy benzophenone, 2,4-dihydroxy benzophenone, 2-hydroxy-4-acryloxy benzophenone, 2-hydroxy-4-(benzyloxy) benzophenone, 2,2′-dihydroxy-4-methoxy benzophenone, 2,2′,4,4′-tetrahydroxy benzophenone, 2,2′-dihydroxy-4,4′-dimoethoxy benzophenone, 2-hydroxy-4-allyloxy benzophenone, 2-hydroxy-4-(2-hydroxyethoxy) benzophenone, and 1,4-bis(4-benzoyl-3-hydroxyphenoxy) butane.

14. The composition according to claim 11, wherein the composition is obtained as a waste plastics stream from post-consumer wastes.

15. A method for reducing fouling and / or corrosion during steam cracking of chemical feeds comprising waste plastics-derived materials, the method comprising steam cracking the composition of polymers according to claim 11.