WO2021133884A1 - Circular economy for plastic waste to polyethylene via refinery fcc and alkylation units - Google Patents
Circular economy for plastic waste to polyethylene via refinery fcc and alkylation units Download PDFInfo
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- WO2021133884A1 WO2021133884A1 PCT/US2020/066796 US2020066796W WO2021133884A1 WO 2021133884 A1 WO2021133884 A1 WO 2021133884A1 US 2020066796 W US2020066796 W US 2020066796W WO 2021133884 A1 WO2021133884 A1 WO 2021133884A1
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- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G1/00—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
- C10G1/002—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal in combination with oil conversion- or refining processes
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- C07C4/04—Thermal processes
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- C08F10/00—Homopolymers and copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond
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- C10G1/00—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
- C10G1/10—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal from rubber or rubber waste
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- C10G11/00—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils
- C10G11/14—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils with preheated moving solid catalysts
- C10G11/18—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils with preheated moving solid catalysts according to the "fluidised-bed" technique
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- C10G9/00—Thermal non-catalytic cracking, in the absence of hydrogen, of hydrocarbon oils
- C10G9/34—Thermal non-catalytic cracking, in the absence of hydrogen, of hydrocarbon oils by direct contact with inert preheated fluids, e.g. with molten metals or salts
- C10G9/36—Thermal non-catalytic cracking, in the absence of hydrogen, of hydrocarbon oils by direct contact with inert preheated fluids, e.g. with molten metals or salts with heated gases or vapours
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- C07C2/54—Preparation of hydrocarbons from hydrocarbons containing a smaller number of carbon atoms by addition of unsaturated hydrocarbons to saturated hydrocarbons or to hydrocarbons containing a six-membered aromatic ring with no unsaturation outside the aromatic ring
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- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
- C10B53/07—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of solid raw materials consisting of synthetic polymeric materials, e.g. tyres
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- C10G2300/00—Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
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- C10G2300/1003—Waste materials
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- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G2300/00—Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
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- C10G2300/1037—Hydrocarbon fractions
- C10G2300/1044—Heavy gasoline or naphtha having a boiling range of about 100 - 180 °C
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- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
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- C10G2300/00—Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
- C10G2300/10—Feedstock materials
- C10G2300/1037—Hydrocarbon fractions
- C10G2300/1048—Middle distillates
- C10G2300/1055—Diesel having a boiling range of about 230 - 330 °C
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- C10G2300/201—Impurities
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- C10G2400/00—Products obtained by processes covered by groups C10G9/00 - C10G69/14
- C10G2400/02—Gasoline
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- C10G2400/00—Products obtained by processes covered by groups C10G9/00 - C10G69/14
- C10G2400/20—C2-C4 olefins
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/143—Feedstock the feedstock being recycled material, e.g. plastics
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
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- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/582—Recycling of unreacted starting or intermediate materials
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Definitions
- a pyrolysis unit produces poor quality products containing contaminants, such as calcium, magnesium, chlorides, nitrogen, sulfur, dienes, and heavy components, which products cannot be used in large quantity for blending in transportation fuels. It has been discovered that by having these products go through the refinery units, the contaminants can be captured in pre-treating units and their negative impacts diminished.
- the fuel components can be further upgraded with appropriate refinery units with chemical conversion processes, with the final transportation fuels produced by the integrated process being of higher quality and meeting the fuels quality requirements.
- the present process will upgrade the wax into valuable gasoline and diesel.
- the integrated process will generate much cleaner naphtha or LPG stream as steam cracker feedstock for ethylene generation and polyethylene production.
- the carbon in and out of the refinery operations are “transparent,” meaning that all the molecules from the waste plastic do not necessarily end up in the exact olefin product cycled back to the polyolefin plants, but are nevertheless assumed as “credit” as the net “green” carbon in and out of the refinery is positive. With these integrated processes, the amount of virgin feeds needed for polyethylene plants will be reduced substantially.
- the preferred starting material for the present process is sorted waste plastics containing predominantly polyethylene and polypropylene (plastics recycle classification types 2, 4, and 5).
- the pre-sorted waste plastics are washed and shredded or pelleted to feed to a pyrolysis unit for thermal cracking.
- FIG. 3 depicts the plastic type classification for waste plastics recycling.
- Classification types 2, 4, and 5 are high density polyethylene, low density polyethylene and polypropylene, respectively. Any combination of the polyethylene and polypropylene waste plastics can be used.
- at least some polyethylene waste plastic is preferred.
- Plastics waste containing polyethylene terephthalate (plastics recycle classification type 1), polyvinyl chloride (plastics recycle classification type 3) and other polymers (plastics recycle classification type 7) need to be sorted out to less than 5%, preferably less than 1% and most preferably less than 0.1%.
- the present process can tolerate a moderate amount of polystyrene (plastics recycle classification type 6).
- Waste polystyrene needs to be sorted out to less than 30%, preferably less than 20% and most preferably less than 5%.
- the pyrolyzing is carried out by contacting a plastic material feedstock in a pyrolysis zone at pyrolysis conditions, where at least a portion of the feed(s) is cracked, thus forming a pyrolysis zone effluent comprising primarily olefins and paraffins.
- Pyrolysis conditions include a temperature of from about 400° C to about 700° C, preferably from about 450° C to about 650° C.
- Conventional pyrolysis technology teaches operating conditions of above- atmospheric pressures. See e.g., U.S. Pat. No. 4,642,401. Additionally, it has been discovered that by adjusting the pressure downward, the yield of a desired product can be controlled. See, e.g., U.S. Pat. No. 6,150,577. Accordingly, in some embodiments where such control is desired, the pyrolysis pressure is sub-atmospheric.
- the steam cracker and ethylene polymerization unit is preferably located near the refinery so that the feedstocks (propane, butane, naphtha, or propane/propylene mix) can be transferred via pipeline.
- the feedstock can be delivered via truck, barge, rail car, or pipeline.
- a naphtha (C Cx) fraction 38 is recovered from the alkylation unit 31.
- This stream 38 can also be fed to a steam cracker 34 for the production of ethylene 37, and subsequent ethylene polymerization 40.
- Polyethylene products 41 can then be made from the polyethylene.
- Example 1 Properties of Pyrolysis Oil and Wax From Commercial Sources
- Pyrolysis oil and wax samples were obtained from commercial sources and their properties are summarized in Table 1. These pyrolysis samples were prepared from waste plastics containing mostly polyethylene and polypropylene via thermal decomposition in a pyrolysis reactor at around 400-600° C, near atmospheric pressure without any added gas or a catalyst.
- a pyrolysis unit typically produces gas, liquid oil product, optionally wax product, and char.
- the pyrolysis unit ’s overhead gas stream containing thermally cracked hydrocarbon was cooled to collect condensate as pyrolysis oil (liquid at ambient temperature) and/or pyrolysis wax (solid at ambient temperature).
- the pyrolysis oil is the main product of the pyrolysis units. Some units produce pyrolysis wax as a separate product in addition to the pyrolysis oil.
- ASTM D4052 method was used for specific gravity measurements. Simulated boiling point distribution curve was obtained using ASTM D2887 method. Carlo-Erba analysis for carbon and hydrogen was based on ASTM D5291 method. Bromine number measurement was based on ASTM D1159 method. Hydrocarbon-type analysis was done using a high resolution magnetic mass spectrometer using the magnet scanned from 40 to 500 Daltons. Total sulfur was determined using XRF per ASTM D2622 method. The nitrogen was determined using a modified ASTM D5762 method using chemiluminescence detection. The total chloride content was measured using combustion ion chromatography instrument using modified ASTM 7359 method.
- the oxygen content in naphtha and distillate boiling range was estimated using GC by GC/MS measurements with electron ionization detector for m/Z range of 29-500. Trace metal and non-metal elements in oil were determined using inductively coupled plasma-atomic emission spectrometry (ICP-AES).
- ICP-AES inductively coupled plasma-atomic emission spectrometry
- Industrial pyrolysis process of sorted plastics sourced predominantly from polyethylene and polypropylene waste, produced quality hydrocarbon streams with specific gravity ranging 0.7 to 0.9, and a boiling range from 18 to 1100° F as in pyrolysis oil or pyrolysis wax.
- the pyrolysis product is rather pure hydrocarbon made of mostly carbon and hydrogen.
- the hydrogen to carbon molar ratio varies from 1.7 to near 2.0.
- the Bromine Number is in the range of 14 through 60 indicating varying degrees of unsaturation coming from olefins and aromatics.
- the aromatic content is in the range of 5 to 23 volume % with a higher severity unit producing more aromatics.
- the pyrolysis products show paraffinic content ranging from mid-20 vol. % to mid-50 vol. %.
- the pyrolysis product contains a substantial amount of olefins.
- Example 2 Fractionation of Pyrolysis Oil for Evaluation As Transportation Fuel
- Sample D was distilled to produce hydrocarbon cuts representing gasoline (350° F ), jet (350 - 572° F), diesel (572 - 700° F) and the heavy (700° F + ) fractions.
- Table 2 summarizes the boiling point distribution and impurity distributions among the distilled product fractions.
- Example 3 Evaluation of Pyrolysis Oil Cut for Gasoline Fuel
- Sample F a pyrolysis oil cut for gasoline fuel boiling range, was evaluated to assess its potential to use as gasoline fuel.
- Sample F has the carbon number range of C5 - C12, typical of the gasoline fuel.
- Sample F a pyrolysis oil cut for gasoline fuel boiling range, cannot be used by itself as automotive gasoline fuel due to its poor quality.
- the gasoline fraction from the pyrolysis oil showed very poor oxidation stability in that Sample F failed only after 90 min compared to the target stability of longer than 1440 minutes.
- the pyrolysis gasoline exceeded the wash gum target of 4 mg/ 100 mL suggesting severe gum forming tendency.
- the pyrolysis gasoline has poor octane numbers compared to the reference gasoline. A premium unleaded gasoline was used as the reference gasoline.
- Example 4 Evaluation of Pyrolysis Oil Cut for Jet Fuel
- Results from Table 1 showed that industrial pyrolysis process of sorted plastics, sourced predominantly from polyethylene and polypropylene waste, produced quality pyrolysis oil or pyrolysis wax made of mostly carbon and hydrogen. With good sorting and efficient pyrolysis unit operation, the nitrogen and sulfur impurities are at low enough levels that a modem refinery can handle cofeeding of pyrolysis feedstocks to their processing units with no detrimental impacts.
- the pyrolysis oil and wax are converted into offgas, LPG paraffins and olefins, FCC gasoline and heavy hydrocarbon components.
- the FCC gasoline is a valuable gasoline blending component.
- the LPG paraffins and olefins are processed further in an alkylation unit to make alkylate gasoline, another valuable gasoline blending component.
- the C3 propane/propylene mix is separated from the FCC unit and purified via the FCC light-end recovery and gas treating units and then fed to a steam cracker.
- Examples 7 and 8 demonstrate the conversion of waste plastics pyrolysis product into quality transportation fuel in a refinery conversion unit, using a FCC unit as an example.
- VGO Vacuum gas oil
- the FCC experiments were carried out on a Model C ACE (advanced cracking evaluation) unit fabricated by Kayser Technology Inc. using regenerated equilibrium catalyst (Ecat) from a refinery.
- the reactor was a fixed fluidized reactor using N2 as fluidization gas.
- Catalytic cracking experiments were carried out at the atmospheric pressure and 900° F reactor temperature. The cat/oil ratio was varied between 5 to 8 by varying the amount of the catalyst.
- a gas product was collected and analyzed using a refinery gas analyzer (RGA), equipped with GC with FID detector. In-situ regeneration of a spent catalyst was carried out in the presence of air at 1300° F, and the regeneration flue gas was passed through a LECO unit to determine the coke yield.
- RAA refinery gas analyzer
- the FCC unit cracks the pyrolysis oil info fuel range hydrocarbons, reduces impurities, and isomerize n-paraffms to isoparaffins. All these chemistry will improve the fuel properties of the pyrolysis oil and wax.
- a zeolite catalyst By cofeeding the pyrolysis oil through the FCC process unit with a zeolite catalyst, the oxygen and nitrogen impurities in the fuel range were reduced substantially, from about 300-1400 ppmN to about 30 ppmN and from about 250-540 ppm O to about 60-80 ppm O.
- the hydrocarbon composition of all these cofeeding products are well within the typical FCC gasoline range.
- Example 8 Coprocessing of Pyrolysis Wax in FCC
- Example 9 Feeding of LPG Olefins from FCC Unit, Which Coprocessed Waste Plastics Pyrolysis Product, to Refinery Alkylation Unit
- the pyrolysis oil cofeeding to a refinery FCC unit produces a substantial amount C3 - C5 olefins with a recycle content.
- the C4 only, C3 - C4 or C3 - C5 stream containing recycled olefins is separated from FCC light-end recovery units, and then fed to an alkylation unit.
- Reaction of LPG olefins and isobutane in the alkylation reactor produces propane, butane and alkylate gasoline.
- Alkylate gasoline is a very valuable gasoline blending component.
- the clean propane, butane, and naphtha streams from the alkylation unit are valuable feedstocks for a steam cracker.
- Example 10 Feeding of Recycled C3-C4 and/or Naphtha to Steam Cracker for Ethylene Production, followeded by Productions of Polyethylene Resin and Polyethylene Consumer Products
- the propane, butane and naphtha streams produced via cofeeding of pyrolysis products to a FCC unit and then to an alkylation unit per Examples 8 and 9 are good feedstock to cofeed to a steam cracker for production of ethylene with a recycle content.
- the C3 propane and propylene steam is recovered from the FCC unit and then purified in the FCC light-end recovery units and then cofed to a steam cracker for production of ethylene with a recycle content. At least a portion of the streams, if not all, are fed to the steam cracker.
- the ethylene is then processed to a polymerization unit to produce polyethylene resin containing some recycled-polyethylene/ polypropylene derived materials while the quality of the newly produced polyethylene is indistinguishable to the virgin polyethylene made entirely from virgin petroleum resources.
- the polyethylene resin with the recycled material is then further processed to produce various polyethylene products to fit the needs of consumer products.
- polyethylene consumer products now contains chemically recycled, circular polymer while quality of the polyethylene consumer products are indistinguishable from those made entirely from virgin polyethylene polymer.
- chemically recycled polymer products are different from the mechanically recycled polymer products whose qualities are inferior to the polymer products made from virgin polymers.
- the word “comprises” or “comprising” is intended as an open- ended transition meaning the inclusion of the named elements, but not necessarily excluding other unnamed elements.
- the phrase “consists essentially of’ or “consisting essentially of’ is intended to mean the exclusion of other elements of any essential significance to the composition.
- the phrase “consisting of’ or “consists of’ is intended as a transition meaning the exclusion of all but the recited elements with the exception of only minor traces of impurities.
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Priority Applications (8)
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| EP24200399.4A EP4458793B1 (en) | 2019-12-23 | 2020-12-23 | Circular economy for plastic waste to polyethylene via refinery fcc and alkylation units |
| CN202080089638.0A CN114846118B (zh) | 2019-12-23 | 2020-12-23 | 通过炼油厂fcc和烷基化单元将塑料废物转化为聚乙烯的循环经济 |
| KR1020227024206A KR20220117902A (ko) | 2019-12-23 | 2020-12-23 | 정제 fcc 및 알킬화 장치를 통한 플라스틱 폐기물의 폴리에틸렌으로의 순환 경제 |
| JP2022538700A JP7623382B2 (ja) | 2019-12-23 | 2020-12-23 | 精製fcc及びアルキレーションユニットを介したポリエチレンへの廃プラスチックのサーキュラーエコノミー |
| CA3164239A CA3164239C (en) | 2019-12-23 | 2020-12-23 | Circular economy for plastic waste to polyethylene via refinery fcc and alkylation units |
| MX2022007242A MX2022007242A (es) | 2019-12-23 | 2020-12-23 | Economia circular para residuos plasticos en polietileno a traves de craqueo catalitico de fluidos (fcc) de refineria y unidades de alquilacion. |
| BR112022011770A BR112022011770A2 (pt) | 2019-12-23 | 2020-12-23 | Economia circular para resíduos de plástico para polietileno via fcc de refinaria e a unidades de alquilação |
| EP20907412.9A EP4081619B1 (en) | 2019-12-23 | 2020-12-23 | Circular economy for plastic waste to polyethylene via refinery fcc and alkylation units |
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| US201962952664P | 2019-12-23 | 2019-12-23 | |
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| PCT/US2020/066796 Ceased WO2021133884A1 (en) | 2019-12-23 | 2020-12-23 | Circular economy for plastic waste to polyethylene via refinery fcc and alkylation units |
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| US (2) | US11518944B2 (https=) |
| EP (2) | EP4458793B1 (https=) |
| JP (1) | JP7623382B2 (https=) |
| KR (1) | KR20220117902A (https=) |
| CN (1) | CN114846118B (https=) |
| BR (1) | BR112022011770A2 (https=) |
| MX (1) | MX2022007242A (https=) |
| WO (1) | WO2021133884A1 (https=) |
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| EP4504853A4 (en) * | 2022-04-01 | 2026-03-18 | Chevron Usa Inc | CIRCULAR ECONOMY OF POLYPROPYLENE PLASTIC WASTE THROUGH AN FCC-CERTIFIED REFINERY UNIT |
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2020
- 2020-12-23 MX MX2022007242A patent/MX2022007242A/es unknown
- 2020-12-23 KR KR1020227024206A patent/KR20220117902A/ko active Pending
- 2020-12-23 EP EP24200399.4A patent/EP4458793B1/en active Active
- 2020-12-23 BR BR112022011770A patent/BR112022011770A2/pt unknown
- 2020-12-23 CN CN202080089638.0A patent/CN114846118B/zh active Active
- 2020-12-23 US US17/131,845 patent/US11518944B2/en active Active
- 2020-12-23 EP EP20907412.9A patent/EP4081619B1/en active Active
- 2020-12-23 JP JP2022538700A patent/JP7623382B2/ja active Active
- 2020-12-23 WO PCT/US2020/066796 patent/WO2021133884A1/en not_active Ceased
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Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2023534223A (ja) * | 2020-07-11 | 2023-08-08 | ユーオーピー エルエルシー | 分解ユニットを用いた統合回収によるプラスチックのモノマーへの変換 |
| JP7603140B2 (ja) | 2020-07-11 | 2024-12-19 | ユーオーピー エルエルシー | 分解ユニットを用いた統合回収によるプラスチックのモノマーへの変換 |
| EP4504852A4 (en) * | 2022-04-01 | 2026-03-18 | Chevron Usa Inc | CIRCULAR ECONOMY OF POLYETHYLENE PLASTIC WASTE THROUGH AN FCC-CERTIFIED REFINERY UNIT |
| EP4504853A4 (en) * | 2022-04-01 | 2026-03-18 | Chevron Usa Inc | CIRCULAR ECONOMY OF POLYPROPYLENE PLASTIC WASTE THROUGH AN FCC-CERTIFIED REFINERY UNIT |
| WO2024218310A2 (en) | 2023-04-19 | 2024-10-24 | Frank Riedewald | Advanced chemical recycling of mixed and pure waste plastics within a molten metal reactor |
Also Published As
| Publication number | Publication date |
|---|---|
| CN114846118A (zh) | 2022-08-02 |
| JP7623382B2 (ja) | 2025-01-28 |
| MX2022007242A (es) | 2022-10-27 |
| EP4081619A4 (en) | 2024-04-10 |
| EP4458793B1 (en) | 2025-11-12 |
| EP4458793A2 (en) | 2024-11-06 |
| KR20220117902A (ko) | 2022-08-24 |
| US20210189251A1 (en) | 2021-06-24 |
| BR112022011770A2 (pt) | 2022-08-30 |
| US11905466B2 (en) | 2024-02-20 |
| EP4081619A1 (en) | 2022-11-02 |
| US11518944B2 (en) | 2022-12-06 |
| JP2023508353A (ja) | 2023-03-02 |
| CA3164239A1 (en) | 2021-07-01 |
| EP4458793A3 (en) | 2024-12-25 |
| EP4081619B1 (en) | 2024-10-09 |
| CN114846118B (zh) | 2023-12-01 |
| US20230079004A1 (en) | 2023-03-16 |
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