WO2024020510A2 - Methods for modifying asphalt using low greenhouse gas liquids obtained from depolymerization of waste plastics - Google Patents
Methods for modifying asphalt using low greenhouse gas liquids obtained from depolymerization of waste plastics Download PDFInfo
- Publication number
- WO2024020510A2 WO2024020510A2 PCT/US2023/070632 US2023070632W WO2024020510A2 WO 2024020510 A2 WO2024020510 A2 WO 2024020510A2 US 2023070632 W US2023070632 W US 2023070632W WO 2024020510 A2 WO2024020510 A2 WO 2024020510A2
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- asphalt
- depolymerization
- mixture
- depolymerized
- asphalt modifier
- Prior art date
Links
- 239000010426 asphalt Substances 0.000 title claims abstract description 136
- 229920003023 plastic Polymers 0.000 title claims abstract description 43
- 239000004033 plastic Substances 0.000 title claims abstract description 43
- 239000002699 waste material Substances 0.000 title claims abstract description 31
- 238000000034 method Methods 0.000 title claims description 74
- 239000007788 liquid Substances 0.000 title abstract description 67
- 239000005431 greenhouse gas Substances 0.000 title abstract description 10
- 239000000463 material Substances 0.000 claims abstract description 96
- 239000000203 mixture Substances 0.000 claims abstract description 66
- 239000011230 binding agent Substances 0.000 claims abstract description 51
- 239000007787 solid Substances 0.000 claims abstract description 44
- 239000003607 modifier Substances 0.000 claims abstract description 42
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 26
- 239000000654 additive Substances 0.000 claims abstract description 23
- 230000008569 process Effects 0.000 claims description 35
- 239000003921 oil Substances 0.000 claims description 25
- 235000019198 oils Nutrition 0.000 claims description 25
- 239000003054 catalyst Substances 0.000 claims description 23
- 238000009834 vaporization Methods 0.000 claims description 21
- 230000008016 vaporization Effects 0.000 claims description 21
- 239000011344 liquid material Substances 0.000 claims description 17
- 238000002156 mixing Methods 0.000 claims description 17
- 239000011384 asphalt concrete Substances 0.000 claims description 15
- 125000003118 aryl group Chemical group 0.000 claims description 14
- 238000004519 manufacturing process Methods 0.000 claims description 12
- 230000000996 additive effect Effects 0.000 claims description 11
- 229920001971 elastomer Polymers 0.000 claims description 9
- 239000011364 vaporized material Substances 0.000 claims description 9
- 238000006243 chemical reaction Methods 0.000 claims description 8
- 239000011261 inert gas Substances 0.000 claims description 8
- 239000002028 Biomass Substances 0.000 claims description 7
- 229910052760 oxygen Inorganic materials 0.000 claims description 7
- 125000001931 aliphatic group Chemical group 0.000 claims description 6
- 239000000446 fuel Substances 0.000 claims description 6
- 239000004606 Fillers/Extenders Substances 0.000 claims description 5
- 229920000034 Plastomer Polymers 0.000 claims description 5
- 150000001412 amines Chemical class 0.000 claims description 5
- 239000010692 aromatic oil Substances 0.000 claims description 5
- 230000000694 effects Effects 0.000 claims description 5
- 239000000806 elastomer Substances 0.000 claims description 5
- 239000000284 extract Substances 0.000 claims description 5
- 239000000945 filler Substances 0.000 claims description 5
- 238000010438 heat treatment Methods 0.000 claims description 5
- 239000010705 motor oil Substances 0.000 claims description 5
- 150000003014 phosphoric acid esters Chemical class 0.000 claims description 5
- 229920000137 polyphosphoric acid Polymers 0.000 claims description 5
- 239000004576 sand Substances 0.000 claims description 5
- QAOWNCQODCNURD-UHFFFAOYSA-N sulfuric acid group Chemical class S(O)(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 5
- 235000015112 vegetable and seed oil Nutrition 0.000 claims description 5
- 239000008158 vegetable oil Substances 0.000 claims description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 4
- 238000012691 depolymerization reaction Methods 0.000 claims description 4
- 238000001035 drying Methods 0.000 claims description 4
- 239000001301 oxygen Substances 0.000 claims description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 4
- 229910021536 Zeolite Inorganic materials 0.000 claims description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 3
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 3
- 239000003995 emulsifying agent Substances 0.000 claims description 3
- 229910044991 metal oxide Inorganic materials 0.000 claims description 3
- 150000004706 metal oxides Chemical class 0.000 claims description 3
- 239000010457 zeolite Substances 0.000 claims description 3
- 239000002184 metal Substances 0.000 claims description 2
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 claims description 2
- 239000011368 organic material Substances 0.000 claims 7
- 238000005194 fractionation Methods 0.000 claims 3
- 238000004381 surface treatment Methods 0.000 claims 2
- 239000002904 solvent Substances 0.000 claims 1
- 229910052799 carbon Inorganic materials 0.000 abstract description 22
- 238000009472 formulation Methods 0.000 abstract description 10
- 239000007795 chemical reaction product Substances 0.000 abstract description 5
- 230000032683 aging Effects 0.000 abstract description 4
- 230000001627 detrimental effect Effects 0.000 abstract description 2
- 239000000047 product Substances 0.000 description 36
- 238000000197 pyrolysis Methods 0.000 description 19
- 230000003716 rejuvenation Effects 0.000 description 11
- 239000007789 gas Substances 0.000 description 8
- 239000004800 polyvinyl chloride Substances 0.000 description 8
- 241000894007 species Species 0.000 description 8
- 239000001993 wax Substances 0.000 description 8
- 230000009467 reduction Effects 0.000 description 7
- 229920000915 polyvinyl chloride Polymers 0.000 description 6
- 238000010926 purge Methods 0.000 description 5
- 238000012360 testing method Methods 0.000 description 5
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 4
- 230000003197 catalytic effect Effects 0.000 description 4
- 238000009826 distribution Methods 0.000 description 4
- 125000000524 functional group Chemical group 0.000 description 4
- 239000012263 liquid product Substances 0.000 description 4
- 229910052757 nitrogen Inorganic materials 0.000 description 4
- 150000002894 organic compounds Chemical class 0.000 description 4
- 238000012545 processing Methods 0.000 description 4
- 239000012265 solid product Substances 0.000 description 4
- 239000002910 solid waste Substances 0.000 description 4
- 244000144725 Amygdalus communis Species 0.000 description 3
- 235000011437 Amygdalus communis Nutrition 0.000 description 3
- 235000020224 almond Nutrition 0.000 description 3
- 238000009833 condensation Methods 0.000 description 3
- 230000005494 condensation Effects 0.000 description 3
- 238000010276 construction Methods 0.000 description 3
- 229930195733 hydrocarbon Natural products 0.000 description 3
- 150000002430 hydrocarbons Chemical class 0.000 description 3
- 239000001257 hydrogen Substances 0.000 description 3
- 229910052739 hydrogen Inorganic materials 0.000 description 3
- 238000011068 loading method Methods 0.000 description 3
- 239000010812 mixed waste Substances 0.000 description 3
- 238000012986 modification Methods 0.000 description 3
- 230000004048 modification Effects 0.000 description 3
- 229920003052 natural elastomer Polymers 0.000 description 3
- 229920001194 natural rubber Polymers 0.000 description 3
- 239000003208 petroleum Substances 0.000 description 3
- 229920002635 polyurethane Polymers 0.000 description 3
- 239000004814 polyurethane Substances 0.000 description 3
- 230000035484 reaction time Effects 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 2
- 239000004743 Polypropylene Substances 0.000 description 2
- 239000004793 Polystyrene Substances 0.000 description 2
- 239000002154 agricultural waste Substances 0.000 description 2
- 238000013459 approach Methods 0.000 description 2
- 239000000470 constituent Substances 0.000 description 2
- 230000003247 decreasing effect Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 239000011491 glass wool Substances 0.000 description 2
- 229920001903 high density polyethylene Polymers 0.000 description 2
- 239000004700 high-density polyethylene Substances 0.000 description 2
- 229920001684 low density polyethylene Polymers 0.000 description 2
- 239000004702 low-density polyethylene Substances 0.000 description 2
- 238000005504 petroleum refining Methods 0.000 description 2
- 239000013502 plastic waste Substances 0.000 description 2
- 239000004014 plasticizer Substances 0.000 description 2
- 229920000728 polyester Polymers 0.000 description 2
- -1 polyethylene terephthalate Polymers 0.000 description 2
- 229920000139 polyethylene terephthalate Polymers 0.000 description 2
- 239000005020 polyethylene terephthalate Substances 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 229920001155 polypropylene Polymers 0.000 description 2
- 229920002223 polystyrene Polymers 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000007858 starting material Substances 0.000 description 2
- 230000002195 synergetic effect Effects 0.000 description 2
- 229920003051 synthetic elastomer Polymers 0.000 description 2
- 239000005061 synthetic rubber Substances 0.000 description 2
- MJYQFWSXKFLTAY-OVEQLNGDSA-N (2r,3r)-2,3-bis[(4-hydroxy-3-methoxyphenyl)methyl]butane-1,4-diol;(2r,3r,4s,5s,6r)-6-(hydroxymethyl)oxane-2,3,4,5-tetrol Chemical compound OC[C@H]1O[C@@H](O)[C@H](O)[C@@H](O)[C@@H]1O.C1=C(O)C(OC)=CC(C[C@@H](CO)[C@H](CO)CC=2C=C(OC)C(O)=CC=2)=C1 MJYQFWSXKFLTAY-OVEQLNGDSA-N 0.000 description 1
- 244000025254 Cannabis sativa Species 0.000 description 1
- 235000012766 Cannabis sativa ssp. sativa var. sativa Nutrition 0.000 description 1
- 235000012765 Cannabis sativa ssp. sativa var. spontanea Nutrition 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 229920002209 Crumb rubber Polymers 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 244000043261 Hevea brasiliensis Species 0.000 description 1
- 229920010126 Linear Low Density Polyethylene (LLDPE) Polymers 0.000 description 1
- 239000004721 Polyphenylene oxide Substances 0.000 description 1
- 244000294611 Punica granatum Species 0.000 description 1
- 235000014360 Punica granatum Nutrition 0.000 description 1
- 239000004902 Softening Agent Substances 0.000 description 1
- 150000007824 aliphatic compounds Chemical class 0.000 description 1
- 150000001338 aliphatic hydrocarbons Chemical class 0.000 description 1
- 125000003368 amide group Chemical group 0.000 description 1
- 150000001491 aromatic compounds Chemical class 0.000 description 1
- 150000004945 aromatic hydrocarbons Chemical class 0.000 description 1
- 239000012075 bio-oil Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 235000009120 camo Nutrition 0.000 description 1
- 150000001721 carbon Chemical class 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 235000005607 chanvre indien Nutrition 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000012612 commercial material Substances 0.000 description 1
- 239000013065 commercial product Substances 0.000 description 1
- 238000005056 compaction Methods 0.000 description 1
- 238000010924 continuous production Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 125000004122 cyclic group Chemical group 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 239000002283 diesel fuel Substances 0.000 description 1
- 239000004815 dispersion polymer Substances 0.000 description 1
- 230000001804 emulsifying effect Effects 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 150000002148 esters Chemical class 0.000 description 1
- 238000011066 ex-situ storage Methods 0.000 description 1
- YMTINGFKWWXKFG-UHFFFAOYSA-N fenofibrate Chemical compound C1=CC(OC(C)(C)C(=O)OC(C)C)=CC=C1C(=O)C1=CC=C(Cl)C=C1 YMTINGFKWWXKFG-UHFFFAOYSA-N 0.000 description 1
- 235000004426 flaxseed Nutrition 0.000 description 1
- 238000004508 fractional distillation Methods 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 239000003502 gasoline Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 239000011487 hemp Substances 0.000 description 1
- 150000002391 heterocyclic compounds Chemical class 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 239000006259 organic additive Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000005453 pelletization Methods 0.000 description 1
- 239000011846 petroleum-based material Substances 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 150000002989 phenols Chemical class 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 229920002857 polybutadiene Polymers 0.000 description 1
- 229920000570 polyether Polymers 0.000 description 1
- 229920001195 polyisoprene Polymers 0.000 description 1
- 229920000098 polyolefin Polymers 0.000 description 1
- 235000013824 polyphenols Nutrition 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000012925 reference material Substances 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 238000005096 rolling process Methods 0.000 description 1
- 239000007790 solid phase Substances 0.000 description 1
- 239000003381 stabilizer Substances 0.000 description 1
- 230000000087 stabilizing effect Effects 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 230000009897 systematic effect Effects 0.000 description 1
- 238000004227 thermal cracking Methods 0.000 description 1
- 229920001169 thermoplastic Polymers 0.000 description 1
- 239000004416 thermosoftening plastic Substances 0.000 description 1
- 239000010409 thin film Substances 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 229940055755 tricor Drugs 0.000 description 1
- 235000013311 vegetables Nutrition 0.000 description 1
- 230000000007 visual effect Effects 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- 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
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B57/00—Other carbonising or coking processes; Features of destructive distillation processes in general
- C10B57/04—Other carbonising or coking processes; Features of destructive distillation processes in general using charges of special composition
- C10B57/06—Other carbonising or coking processes; Features of destructive distillation processes in general using charges of special composition containing additives
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- 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
- C10G1/10—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
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08L—COMPOSITIONS OF MACROMOLECULAR COMPOUNDS
- C08L95/00—Compositions of bituminous materials, e.g. asphalt, tar, pitch
Definitions
- This invention relates to environmentally friendly, low greenhouse gas (GHG) asphalt modifiers.
- GSG low greenhouse gas
- the invention discloses carbon efficient liquid products derived from thermal depolymerization of waste plastics and/or other organic feedstocks and methods for modifying asphalt/bitumen products using said liquid products, singularly or together with other modifiers, to yield better performing, environmentally friendly asphalt pavement.
- the asphalt binder used for paving and industrial uses is a solid or semi-solid bituminous material.
- Such asphalt binder is either naturally occurring or derived from petroleum refining processes and includes a variety of paraffinic and aromatic hydrocarbons and heterocyclic compounds.
- Asphalt binder is a commonly used material for construction purposes such as roofing materials, water and damp-proofing products, bridge decks, racetracks, airport runways, parking lots, bicycle paths, and port facilities. A majority of asphalt binder is used in roadway and pavement applications. When asphalt binder is mixed with aggregate and used for paving it is called asphalt concrete mixture or simply asphalt pavement.
- asphalt formulations incorporating unmodified asphalt binder may exhibit a poor performance grade rating (PG Rating) for pavements designed for high vehicular traffic or loading or severe climate zones. Temperatures and traffic conditions outside the pavement design range lead to deterioration of the asphalt pavement and short service life.
- PG Rating performance grade rating
- petroleum refining processes have become optimized to produce lighter liquid-range products (e.g., gasoline, diesel fuel, etc.)
- the resulting bottoms from which asphalt binders are derived have decreased in volume and become heavier, which further exacerbates the PG Rating problem.
- additives commonly include: petroleum extracts, waste motor oils and waste vegetable and soy oils.
- additive(s) and “modifier(s)” convey similar meanings and are used interchangeably herein.
- More than 90% of the carbon footprint of asphalt roads is attributable to the production and transport of the constituent materials (asphalt binder, petroleum-derived additives, and aggregate) and formulation (e.g., high-temperature mixing) and transport of the hot asphalt mixture to the paving site.
- Waste plastics are non-degradable constituents that can stay in the environment for centuries. Their large land space consumption is unsafe to humans and animals. Concomitantly, the continuous production of plastics poses another problem as they are petroleum-based material and thus contribute to depletion of the finite petroleum resources. In theory, the thermoplastic component of the polymeric solid waste stream can be recovered, segregated, and recycled into new useful products. In practice, however, only a small fraction of polymeric solid wastes are ultimately recycled, and there has not been a technology that can consume a large amount of such plastic waste and contribute to carbon footprint reduction in a significant way.
- a low-cost method of producing additives that can be employed to achieve improved processing and more desirable physical characteristics of asphalt compositions, while ensuring good blending of the new asphalt and added RAP material, would be commercially and environmentally advantageous. Such a method would ideally employ a readily available, inexpensive feedstock, preferably recyclable material, and employ an economical process. In addition to reducing cost, it is also preferred to produce additives that yield an overall lower carbon footprint, including, for example: (1) an environmentally friendly additive with a zero or negative footprint in its own production and (2) an additive that, when utilized in an asphalt mixture, enables a reduced carbon footprint in the overall paving process.
- the present invention relates to asphalt materials with enhanced performance and tolerance against detrimental effects from aging and temperature, through use of a liquid or liquid mixture formed by a plastic depolymerization process, singularly or together with other modifiers, as an additive/modifier.
- the asphalt herein to be modified can be asphalt binder (bitumen) or recycled asphalt pavement (RAP).
- Bitumen asphalt binder
- RAP recycled asphalt pavement
- FIG. 1 is a flowchart illustrating a process for creating depolymerized liquid materials from solid polymeric materials and/or other organic feedstocks
- FIG. 2 is a flowchart illustrating a process for employing depolymerized liquid materials as modifiers in asphalt modification.
- FIG. 3 is a graph showing the product distribution of oil, gas, and solid products from the pyrolysis of representative waste plastic materials YM-1 and YM-2 at different temperatures.
- FIG. 4 is a graph showing the product distribution of oil, gas, and solid products from the co-pyrolysis of representative waste plastic materials YM-1 and YM-3 at 400°C.
- FIG. 5 is a graph showing the product distribution of oil, gas, and solid products from the co-pyrolysis of representative waste plastic materials YM-2 and YM-3 at 400°C.
- FIG. 6 is a graph showing the product distribution of oil, gas, and solid products from the co-pyrolysis of representative waste materials AS and YM-3 at 400°C.
- FIG. 7 is a graph showing the performance of aged asphalt material rejuvenated with a representative depolymerized liquid material of the invention.
- a solid polymeric material or a mixture of solid polymeric materials is heated in a reactor such that said polymeric material anaerobically turns into a vapor form.
- other organic feedstocks may be combined with the polymeric material(s).
- An inert gas stream or an applied vacuum is then utilized to transfer the vaporized material into a reactor where said vaporized material undergoes a thermal depolymerization process to produce a vapor stream consisting of a mixture of depolymerization products.
- a depolymerized liquid material product is collected from the vapor stream by condensation.
- the method can be operated in a batch, continuous, or semi -continuous fashion.
- FIG. 1 A flowchart illustrating an example of an overall process for creating a depolymerized liquid material is shown in FIG. 1.
- the solid polymeric material (1) and other organic feedstock (2), if optionally utilized, are added to reactor (3) where they are vaporized at high temperature under anaerobic conditions.
- the vaporized material is transferred to reactor (4) optionally containing a catalyst to effect the depolymerization reaction.
- the depolymerized vapor stream is then transferred through one or more condensers (5) where the depolymerized liquid materials are collected as liquids.
- each subsequent condenser after the first will generally be cooled at sequentially decreasing temperatures such that the highest molecular weight fractions will condense first (e.g., condenser 5a) and then sequentially lower molecular weight fractions will condense until only gaseous products remain.
- the highest molecular weight fraction or fractions might be waxes at room temperature.
- Gaseous products (6) exit the condensers (5) and can be subsequently captured for future use, flared as waste, or utilized as fuel to provide heat for the process.
- the polymeric material can be one or more polyolefin plastics such as high-density polyethylene (HDPE), low density polyethylene (LDPE), linear low-density polyethylene (LLDPE), and/or polyethylene terephthalate (PET), and/or polypropylene (PP), and/or polyurethanes (PUR) such as polyester and polyether polyurethanes, and/or polystyrenes (PS).
- the polymeric material may comprise polyvinyl chloride (PVC).
- the polymeric material may comprise natural or synthetic rubber materials such as polyisoprenes and polybutadienes.
- the polymeric material may comprise recycled plastics.
- the polymeric materials may comprise various organic additives such as plasticizers and/or stabilizers.
- the polymeric material may be a mixture of one or more or all of the plastics listed above.
- organic feedstocks may be combined with the polymeric material(s) prior to or during depolymerization (in-situ production).
- organic feedstocks may include lignocellulosic feedstocks obtained from biomass resources such as, for example, wood and/or hemp pulp, flaxseed, etc. and/or proteinic feedstocks obtained from plant, animal, and/or algal resources.
- biomass resources such as, for example, wood and/or hemp pulp, flaxseed, etc.
- proteinic feedstocks obtained from plant, animal, and/or algal resources.
- such organic feedstocks are derived from harvested biomass resources.
- such organic feedstocks are derived from wastes or by-products derived from biomass processing operations, such as, for example, sawdust, pomegranate peel and seed, almond shells, etc.
- the amount and composition of such other organic feedstocks are chosen to optimize the amounts of polar functional groups present in the depolymerized liquid material.
- the amount of other organic feedstocks added ranges from about 1-250% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 10-150% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 25-100% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 15-50% by weight relative to the amount of the solid polymeric material.
- the amount of other organic feedstocks added ranges from about 5-50% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 5-25% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 1-10% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 2-6% by weight relative to the amount of the solid polymeric material.
- the solid polymeric materials and the other organic feedstocks may be thermally depolymerized separately (ex-situ production) such that distinct depolymerized liquids are produced.
- the distinct depolymerization liquids may be utilized independently or blended together in various combinations to achieve the desired properties.
- the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 1-200% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material.
- the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 5-150% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material.
- the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 25-100% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 15-50% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. Tn some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 1-20% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material.
- the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 1-10% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 2-6% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material.
- the depolymerization can be a purely thermal reaction or it can employ catalysts. Depending on the starting material and the desired end-product, depolymerization could be employed for a slight or extreme reduction of the molecular weight of the starting material.
- the depolymerization process preferably employs a catalyst.
- the preferred catalyst employs a biochar derived from biomass, an activated carbon material, a metal or metal oxide material, or a zeolite or alumina material. Biochar catalysts are particularly inexpensive and, at the end of their usefulness as catalysts, may be utilized as a component of the modified asphalt blend.
- Zeolite, metal oxide, or alumina catalysts offer high catalytic efficiencies and can be readily regenerated via calcination at high temperatures but are more expensive than biochar materials.
- certain components within the waste plastics or mixtures of waste plastics may act as catalysts or may generate catalytic species during pyrolysis.
- chlorinated plastics, such as PVC, or chlorinated additives may generate chlorine radicals during pyrolysis which may promote a catalytic effect on the pyrolysis of other plastic materials or organic feedstocks that may be present.
- Mixtures of these various catalysts may also be utilized, along with reaction parameters such as temperature, reaction time, and condensation temperature to fine-tune the properties of the resulting depolymerization liquids.
- the combination of other organic feedstocks with the polymeric materials will generate a positive synergistic depolymerization environment requiring lower depolymerization temperatures and, therefore, less energy consumption.
- the synergistic effects of the other organic feedstocks may reduce or even eliminate the need for a depolymerization catalyst to achieve a liquid product with a particular set of properties such as molecular weight, polar content, viscosity, etc.
- the vaporization process and depolymerization process employs two separate reactors.
- One or more of the reactors can include a static mixer.
- An inert gas such as nitrogen can be used to purge oxygen from the reactor and to carry the feedstock vapor from the vaporization reactor to the depolymerization reactor.
- an applied vacuum is utilized to purge oxygen from the reactor and to pull the feedstock vapor from the vaporization reactor to the depolymerization reactor.
- the vaporization process and the depolymerization process may occur within a single reactor.
- the vaporization and depolymerization temperatures are the same. In some embodiments, the vaporization and depolymerization temperatures may be different.
- Temperatures greater than about 250°C are generally required to effect vaporization, depending on the composition of the feedstock.
- vaporization temperatures such as 250-300°C , 3OO-35O°C, 350-400°C, 450-500°C, 500-550°C, 550-600°C, 600-650°C, 650-700°C, 300-400°C, 400-500°C, 500-600°C, or 600-700°C might be utilized.
- vaporization temperatures are between 250-400°C.
- vaporization temperatures are between 400-500°C.
- vaporization temperatures are between 450-550°C.
- vaporization temperatures are between 500-600°C. Temperatures greater than about 250°C are generally desired to effect the thermal depolymerization process, depending on the composition of the feedstock and/or catalyst. In some embodiments, depolymerization temperatures such as 250-300°C , 3OO-35O°C, 350-400°C, 450-500°C, 500-550°C, 550-600°C, 600-650°C, 650-700°C, 300-400°C, 400-500°C, 500-600°C, or 600-700°C might be utilized. In some embodiments, depolymerization temperatures are between 400-500°C. In some embodiments, depolymerization temperatures are between 450-550°C.
- depolymerization temperatures are between 500- 600°C. In some embodiments, depolymerization temperatures are between 550-650°C. In some embodiments, depolymerization temperatures are between 600-700°C.
- the depolymerization process converts the solid polymeric material, alone or in combination with one or more other organic feedstocks, into a mixture of gaseous, liquid, and solid or wax fractions. The proportion of these different components vary with reaction conditions such as reaction temperature, reaction time, and choice of catalyst (including no catalyst). In some embodiments, it is desirable to minimize the amount of the solid or wax fraction by utilizing higher reaction temperatures. Proper choice of catalyst and a reduced reaction time may also decrease wax yield.
- the depolymerization process generally produces a significant amount of gaseous products, especially under conditions intended to minimize wax formation.
- Wax products are less desirable products because they require further processing steps (e.g., grinding, pelletizing, prilling, etc.) to be easily handled and require higher blending temperatures when mixed with asphalt binder.
- Depolymerization conditions favoring low wax also produce higher amounts of aromatics and other unsaturated carbon containing products with concomitant hydrogen gas production.
- Liquid depolymerization products can be better utilized, and help to lower mixing temperatures, in WMA formulations and can help to soften HMA formulations, making them more ductile.
- the gaseous fraction possibly including some of the liquid fraction, as fuel to generate the heat required for the vaporization and/or depolymerization reactor(s).
- the hydrogen produced during depolymerization is a clean burning fuel that does not contribute to carbon emissions.
- a typical molecule in the depolymerized liquid material comprises aromatic rings interconnected with one another directly and/or aromatic rings connected by aliphatic species.
- the preferred ring count is about 2-6. In some embodiments, the preferred ring count is about 2-5. In some embodiments, the preferred ring count is about 2-4.
- the depolymerized liquid material should contain a small percentage of polar oxygen-containing and/or nitrogen-containing compounds, such as esters, phenolic compounds, and derivatives thereof.
- the total heterogeneous element (O, N) in the oil shall be in the range of 1-5% by weight. In some embodiments, the total heterogeneous element (O, N) in the oil shall be in the range of 1-10% by weight. In some embodiments, the total heterogeneous element (O, N) in the oil shall be in the range of 2-6% by weight.
- the depolymerized liquid fraction is generally collected by condensation from the depolymerized vapor stream exiting the reactor(s).
- a single liquid fraction may be obtained by passing the vapor stream through a single condenser set to a sufficiently low temperature to condense a liquid over a desired molecular weight or carbon (C n ) number.
- C n carbon
- lower condenser temperatures will generally be required to condense a liquid of a particular molecular weight or C n range.
- multiple fractions of varying molecular weight may be obtained by passing through a series of condensers at sequentially lower temperatures as described above.
- Any particular depolymerized liquid material fraction may also be further fractionated in a separate step by fractional distillation.
- the present method involves two main concepts: (1) the creation of depolymerized liquid materials via depolymerization of solid plastic materials and/or other organic compounds, and (2) adding these liquids, or a mixture of these liquids, to modify various asphalt compositions.
- the depolymerized liquid modifier(s) can be added during a “wet process” to the asphalt binder, i.e., prior to adding aggregates to the asphalt mixture to produce, for example but not limited to, an improved asphalt binder composition.
- the depolymerized liquid modifier(s) can be added during a “dry process,” i.e., in concurrence with aggregate, RAP, and/or other solid fdler addition.
- FIG. 2 A non-limiting example of a dry process is shown in FIG. 2.
- Depolymerization liquid(s) derived from depolymerization of plastics (7) and/or from depolymerization of other organic compounds (8) are mixed with asphalt binder (9), other common asphalt modifiers (10), and solid fillers such as aggregate (11) and/or RAP (12) at approximately 110-160°C to produce the final asphalt concrete formulation (14).
- the depolymerized liquid modifier(s) can be sprayed on the RAP content prior to mixing the RAP with a virgin asphalt binder.
- ground or shredded waste plastic material which may be the same as or different from the plastic material employed to produce the depolymerization liquid, may be added as a fdler to produce a polymer modified asphalt.
- SBS and/or crumb rubber can be ground up or partially depolymerized in a similar depolymerization process and blended in along with the liquid.
- ground, crushed or shredded RAP and/or recycled asphalt shingle (RAS) may be added to produce a modified asphalt concrete mixture.
- moderate blending temperatures of 100-130°C can be achieved by treating the asphalt binder with the depolymerization liquid prior to adding in aggregates (the liquid can be used as a softening agent for the asphalt binder allowing a WMA process).
- the asphalt product can be further modified by materials such as an elastomer, plastomer, wax, poly phosphoric acid, sulfuric acids, amines, amide-diamine, phosphate esters, hydrolene aromatic oils, extender oils, vegetable oils, asphalt sand, naturally occurring bitumens and/or a combination thereof.
- the modified asphalt product can be subjected to an emulsifying process by mixing in an emulsifier and water.
- the addition of the depolymerized liquid improves the processing and physical characteristics of the modified asphalt, including reduction in blend time and/or blend temperature to achieve optimal or near-optimal dispersion of the polymer fillers and/or dispersion of additional modifier(s), resulting in higher throughputs; enablement of higher RAP and RAS loading through reduced mix stiffness and increased ductility; and compaction and material handling.
- modifiers with high aromatic content and/or polar functional groups such as, for example, phenolics and/or amide groups
- aliphatics and saturated species are effective in softening asphalt binder during blending, and contribute to rutting resistance once applied, hence liquid with aliphatic species can be blended in as an additive to lower the viscosity of asphalt binder during the WMA process.
- the liquid modifiers may incorporate 2-40% by weight of depolymerization liquids derived from organic compounds as such liquids contain enhanced amounts of polar functional groups that can facilitate deagglomeration of asphaltene sheets in asphalt formulations.
- the depolymerization liquids derived from plastic materials will contain small aromatic compounds along with some amount of saturated and unsaturated aliphatic compounds which may aid in dispersing and stabilizing the detangled asphaltene sheets present in a solution.
- the addition of depolymerized liquids improves the physical characteristics of the final asphalt product.
- the resulting final products can have various properties that differ from their unmodified forms.
- the properties include, among other things, improved rutting susceptibility; improved fatigue cracking resistance; improved thermal cracking resistance; improved thermal stability; improved polymer dispersion and viscosity. Improvements to elastomeric properties and energy of deformation are also observed in some embodiments.
- the depolymerization process can be self-fueling and does not require external energy.
- the gaseous product in the depolymerization process in general provides adequate heating energy to self-fuel the ongoing said process.
- it is possible to optimize hydrogen in the gaseous product by keeping reaction temperatures in an desired range in a catalytic reaction, hence emitting mostly H2O as steam (90%+ hydrogen by volume in gaseous product is achievable from experimental data).
- a negative carbon footprint is achievable with biochar-based catalyst (derived from organic products such as agricultural waste) and/or co-depolymerization with an organic product (such as agricultural waste).
- CO2 was sequestered during the growth of the organic product, when used to produce biochar and/or co-depolymerization the originally sequestered carbon is locked in solid phase and/or liquid phase.
- biochar once its catalytic uses are finished, such biochar solid is added into asphalt mixture as a filler, eventually locking up the sequestered CO2.
- the carbon footprint of the depolymerized product is further offset and achieves carbon neutrality, yielding 1 .6 metric tons of CO2 captured from the environment for each ton of waste plastics depolymerized.
- Ground almond shell was obtained from Northern California almond farms. Representative waste plastic materials were obtained from three different types of yoga mat products:
- YM-1 was a yoga mat comprising polyester and natural rubber
- YM-2 was a multilayered yoga mat comprising various plastics along with natural and synthetic rubbers
- YM-3 was a yoga mat comprising polyvinyl chloride (PVC) and associated ester- based plasticizers.
- Representative mixed waste plastic materials YM-1 and YM-2 were pyrolyzed according to the general procedure described above at different pyrolysis temperatures (400°C, 450°C, and 500°C) to yield the mix of depolymerized liquid, solid residue, and gas products as shown in Table 1 and represented graphically in FIG. 3. All of the values shown are an average of three runs. Generally, higher pyrolysis temperatures yielded higher depolymerized liquid and gas yields and reduced residual solid yields.
- a depolymerization liquid was prepared by the co-pyrolysis of 1 : 1 YM-l/YM-3 at 400°C according to the general procedure as in Run 9 of Example 2 above.
- a sample of “aged” asphalt binder was prepared from a virgin bitumen material (“Virgin”) via standard laboratory accelerated aging procedures in a rolling thin film oven pressure vessel to a 10-year field aged equivalent material (“Aged”).
- Samples of rejuvenated asphalt binder were prepared by blending the aged bitumen material with (i) 10% by weight of the inventive depolymerization liquid (“Rejuvenated (I)”) and (ii) 10% by weight of a standard commercial rejuvenating material Reclamite® (Tricor Refining, LLC) (“Rejuvenated (R)”) as a reference material.
- Standard linear amplitude sweep (LAS) testing method AASHTO T 391-20 was run (FIG. 7) to determine the various asphalt binders' resistance to fatigue damage by means of cyclic loading employing systematic, linearly increasing load amplitudes. This test is commonly used to simulate field durability.
- the LAS curves of each binder give a visual estimate of the load bearing performance when compared to one another.
- This invention may be industrially applied to the development, manufacture, and use of an asphalt modifier that is environmentally friendly with low greenhouse gas (GHG), produced by using solid plastic materials, alone or in conjunction with other organic feedstocks, to prepare carbon-efficient asphalt formulations and end-products.
- GOG low greenhouse gas
Abstract
The present invention relates to environmentally friendly, low greenhouse gas (GHG) liquid asphalt modifiers produced via a thermal depolymerization of solid plastic materials, particularly waste plastic materials, alone or in conjunction with other organic feedstocks, and their use to prepare carbon-efficient asphalt formulations and end-products. The carbon-neutral to carbon-negative liquid additives yield asphalt materials with enhanced performance and tolerance against detrimental effects from aging and temperature, along with a reduced carbon-footprint. The liquid modifiers described herein can be used to modify asphalt binders (bitumen) to provide lower temperature processability and/or improved performance and/or to rejuvenate recycled asphalt pavement (RAP) such that less virgin binder and aggregate needs to be produced and transported when repaving. The invention therefore allows waste plastics to be utilized as a desirable feedstock material and lessens the carbon footprint of the resulting asphalt end-products.
Description
METHODS FOR MODIFYING ASPHALT USING LOW GREENHOUSE GAS LIQUIDS OBTAINED FROM DEPOLYMERIZATION OF WASTE PLASTICS
TECHNICAL FIELD
[0001] This invention relates to environmentally friendly, low greenhouse gas (GHG) asphalt modifiers. Specifically, the invention discloses carbon efficient liquid products derived from thermal depolymerization of waste plastics and/or other organic feedstocks and methods for modifying asphalt/bitumen products using said liquid products, singularly or together with other modifiers, to yield better performing, environmentally friendly asphalt pavement.
BACKGROUND
[0002] Under ambient conditions, the asphalt binder used for paving and industrial uses is a solid or semi-solid bituminous material. Such asphalt binder is either naturally occurring or derived from petroleum refining processes and includes a variety of paraffinic and aromatic hydrocarbons and heterocyclic compounds. Asphalt binder is a commonly used material for construction purposes such as roofing materials, water and damp-proofing products, bridge decks, racetracks, airport runways, parking lots, bicycle paths, and port facilities. A majority of asphalt binder is used in roadway and pavement applications. When asphalt binder is mixed with aggregate and used for paving it is called asphalt concrete mixture or simply asphalt pavement.
[0003] Asphalt alone, however, often does not possess all the physical characteristics desirable for many construction purposes and modifying asphalt is a common practice today. For instance, asphalt formulations incorporating unmodified asphalt binder may exhibit a poor performance grade rating (PG Rating) for pavements designed for high vehicular traffic or loading or severe climate zones. Temperatures and traffic conditions outside the pavement design range lead to deterioration of the asphalt pavement and short service life. Furthermore, as petroleum refining processes have become optimized to produce lighter liquid-range products (e.g., gasoline, diesel fuel, etc.), the resulting bottoms from which asphalt binders are derived have decreased in volume and become heavier, which further exacerbates the PG Rating problem. Hence, it has been an objective to broaden the PG Rating range of asphalt formulations used in road-pavement applications by the addition of various additives to the asphalt binder. Such additives commonly
include: petroleum extracts, waste motor oils and waste vegetable and soy oils. The terms “additive(s)” and “modifier(s)” convey similar meanings and are used interchangeably herein.
[0004] In addition to modifying above-mentioned virgin asphalt binders in the traditional paving process, recent effort to reduce paving carbon footprint has gained much industry wide interest to utilize modifier/additive further to achieve reduced blending temperatures as well as modifying aged binders from recycled asphalt mixtures. Due to the high molecular weight of the molecules present in asphalt binders, relatively high temperatures (135°C-160°C) are required when mixing unmodified asphalt binder with aggregate to produce asphalt pavement. Thus, traditional asphalt pavement formulations are commonly referred to as hot-mix asphalt (HMA). More than 90% of the carbon footprint of asphalt roads is attributable to the production and transport of the constituent materials (asphalt binder, petroleum-derived additives, and aggregate) and formulation (e.g., high-temperature mixing) and transport of the hot asphalt mixture to the paving site. This means that a significant amount of the annual carbon emissions from road construction could be avoided by enabling a process that addresses the method paving materials are produced, formulated, and transported. Currently two approaches have gained major attention: (1) modifying the asphalt binder to lower blending temperature to 105°C-150°C (so called warm-mix asphalt or WMA) to significantly reduce the emissions from burning diesel (or other heating fuels) and (2) incorporating recycled asphalt pavement (RAP) or recycled asphalt shingles (RAS) to reduce the amount of virgin binder and aggregate needed. These two approaches can work individually or can be combined to further reduce carbon footprint. As an example, according to a recent peer reviewed life cycle study (Sustainability 2021, 13(3), 1382; https://doi.org/10.3390/sul3031382), a WMA with 93% RAP content reduces carbon emissions by 55-64% compared with a comparable HMA with virgin aggregate, which translate to 25 Million Metric tons of CO2 emissions per year in the US alone, and 134 Million Metric tons of global CO2 reduced globally.
[0005] Therefore, when repaving asphalt roadways, it is desirable to break up and reuse the old asphalt pavement (the RAP) in the new asphalt concrete mixture. However, due to oxidation and loss of small aromatic molecules, the asphalt binder in the old pavement becomes hard and brittle over time so the RAP must be rejuvenated to improve performance prior to laying the new asphalt concrete containing RAP. One key for incorporating RAP in both the HMA and the
WMA process is to add back lighter, mid-range hydrocarbons with significant aromatic content to revive the physical properties of the asphalt binder. In terms of rheological parameters, the goal is to decrease modulus and increase phase angle to have the rejuvenated asphalt binder meet a specified PG Rating again. However, the additives that are utilized to lower blending temperatures in WMA and to rejuvenate RAP are usually derived from petrochemical processes and carry their own significant carbon footprint.
[0006] Waste plastics are non-degradable constituents that can stay in the environment for centuries. Their large land space consumption is unsafe to humans and animals. Concomitantly, the continuous production of plastics poses another problem as they are petroleum-based material and thus contribute to depletion of the finite petroleum resources. In theory, the thermoplastic component of the polymeric solid waste stream can be recovered, segregated, and recycled into new useful products. In practice, however, only a small fraction of polymeric solid wastes are ultimately recycled, and there has not been a technology that can consume a large amount of such plastic waste and contribute to carbon footprint reduction in a significant way.
[0007] Pyrolysis is an alternate solution that breaks down many common solid waste plastics as well as a wide variety of solid waste biomass materials into more easily handled oils. Although such types of recovered oils could be potentially interesting as modifiers for asphalt modification, prior work has shown poor results in this regard. In terms of oils derived from plastics, efforts have primarily been focused on producing fuel oils comprising light weight aliphatic hydrocarbons for energy recovery. Such oil, however, will not work in asphalt modification due to its low boiling point (poor storage-ability) and excessively strong solvency, which prevents asphalt binder from bonding to aggregate surface. Bio-oils derived from biomass have high polar content and, when added to asphalt, have been found to accelerate binder aging and/or re-aging.
[0008] A low-cost method of producing additives that can be employed to achieve improved processing and more desirable physical characteristics of asphalt compositions, while ensuring good blending of the new asphalt and added RAP material, would be commercially and environmentally advantageous. Such a method would ideally employ a readily available,
inexpensive feedstock, preferably recyclable material, and employ an economical process. In addition to reducing cost, it is also preferred to produce additives that yield an overall lower carbon footprint, including, for example: (1) an environmentally friendly additive with a zero or negative footprint in its own production and (2) an additive that, when utilized in an asphalt mixture, enables a reduced carbon footprint in the overall paving process.
DISCLOSURE OF THE INVENTION
[0009] The present invention relates to asphalt materials with enhanced performance and tolerance against detrimental effects from aging and temperature, through use of a liquid or liquid mixture formed by a plastic depolymerization process, singularly or together with other modifiers, as an additive/modifier. The asphalt herein to be modified can be asphalt binder (bitumen) or recycled asphalt pavement (RAP). Shortcomings of conventional methods of producing additive-modified asphalt are overcome by a method for forming a liquid and employing the liquid to modify asphalt. The present invention also allows waste plastics to be utilized as a desirable feedstock material and lessens the carbon footprint of the resulting asphalt end-products.
BRIEF DESCRIPTION OF THE DRAWINGS
[0010] These and other objects, features and attendant advantages of the present invention will be more fully appreciated or become better understood when considered in conjunction with the accompanying drawings, wherein:
FIG. 1 is a flowchart illustrating a process for creating depolymerized liquid materials from solid polymeric materials and/or other organic feedstocks;
FIG. 2 is a flowchart illustrating a process for employing depolymerized liquid materials as modifiers in asphalt modification.
FIG. 3 is a graph showing the product distribution of oil, gas, and solid products from the pyrolysis of representative waste plastic materials YM-1 and YM-2 at different temperatures.
FIG. 4 is a graph showing the product distribution of oil, gas, and solid products from the
co-pyrolysis of representative waste plastic materials YM-1 and YM-3 at 400°C.
FIG. 5 is a graph showing the product distribution of oil, gas, and solid products from the co-pyrolysis of representative waste plastic materials YM-2 and YM-3 at 400°C.
FIG. 6 is a graph showing the product distribution of oil, gas, and solid products from the co-pyrolysis of representative waste materials AS and YM-3 at 400°C.
FIG. 7 is a graph showing the performance of aged asphalt material rejuvenated with a representative depolymerized liquid material of the invention.
MODES FOR CARRYING OUT THE INVENTION
[0011] The description set forth below in connection with the appended drawings is intended as a description of presently-preferred embodiments of the invention and is not intended to represent the only forms in which the present invention may be constructed or utilized. The description sets forth the functions and the sequence of steps for constructing and operating the invention in connection with the illustrated embodiments. It is to be understood, however, that the same or equivalent functions and sequences may be accomplished by different embodiments that are also intended to be encompassed within the spirit and scope of the invention.
[0012] In the present invention, a solid polymeric material or a mixture of solid polymeric materials is heated in a reactor such that said polymeric material anaerobically turns into a vapor form. In some embodiments of the present invention, other organic feedstocks may be combined with the polymeric material(s). An inert gas stream or an applied vacuum is then utilized to transfer the vaporized material into a reactor where said vaporized material undergoes a thermal depolymerization process to produce a vapor stream consisting of a mixture of depolymerization products. A depolymerized liquid material product is collected from the vapor stream by condensation. The method can be operated in a batch, continuous, or semi -continuous fashion.
[0013] A flowchart illustrating an example of an overall process for creating a depolymerized liquid material is shown in FIG. 1. The solid polymeric material (1) and other organic feedstock
(2), if optionally utilized, are added to reactor (3) where they are vaporized at high temperature under anaerobic conditions. The vaporized material is transferred to reactor (4) optionally containing a catalyst to effect the depolymerization reaction. The depolymerized vapor stream is then transferred through one or more condensers (5) where the depolymerized liquid materials are collected as liquids. If multiple condensers (5) are utilized, each subsequent condenser after the first will generally be cooled at sequentially decreasing temperatures such that the highest molecular weight fractions will condense first (e.g., condenser 5a) and then sequentially lower molecular weight fractions will condense until only gaseous products remain. In some cases, the highest molecular weight fraction or fractions might be waxes at room temperature. Gaseous products (6) exit the condensers (5) and can be subsequently captured for future use, flared as waste, or utilized as fuel to provide heat for the process.
[0014] In some embodiments of the present invention, the polymeric material can be one or more polyolefin plastics such as high-density polyethylene (HDPE), low density polyethylene (LDPE), linear low-density polyethylene (LLDPE), and/or polyethylene terephthalate (PET), and/or polypropylene (PP), and/or polyurethanes (PUR) such as polyester and polyether polyurethanes, and/or polystyrenes (PS). In some embodiments of the present invention, the polymeric material may comprise polyvinyl chloride (PVC). In some embodiments of the present invention, the polymeric material may comprise natural or synthetic rubber materials such as polyisoprenes and polybutadienes. The polymeric material may comprise recycled plastics. In some embodiments of the present invention, the polymeric materials may comprise various organic additives such as plasticizers and/or stabilizers. In some embodiments, the polymeric material may be a mixture of one or more or all of the plastics listed above.
[0015] In some embodiments of the present invention, other organic feedstocks may be combined with the polymeric material(s) prior to or during depolymerization (in-situ production). Without limitation, such organic feedstocks may include lignocellulosic feedstocks obtained from biomass resources such as, for example, wood and/or hemp pulp, flaxseed, etc. and/or proteinic feedstocks obtained from plant, animal, and/or algal resources. In some embodiments of the present invention, such organic feedstocks are derived from harvested biomass resources. In other embodiments, such organic feedstocks are derived from wastes or by-products derived from biomass processing operations, such as, for example, sawdust,
pomegranate peel and seed, almond shells, etc. Tn some embodiments, the amount and composition of such other organic feedstocks are chosen to optimize the amounts of polar functional groups present in the depolymerized liquid material. In some embodiments, the amount of other organic feedstocks added ranges from about 1-250% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 10-150% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 25-100% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 15-50% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 5-50% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 5-25% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 1-10% by weight relative to the amount of the solid polymeric material. In some embodiments, the amount of other organic feedstocks added ranges from about 2-6% by weight relative to the amount of the solid polymeric material.
[0016] In some embodiments of the present invention, the solid polymeric materials and the other organic feedstocks may be thermally depolymerized separately (ex-situ production) such that distinct depolymerized liquids are produced. The distinct depolymerization liquids may be utilized independently or blended together in various combinations to achieve the desired properties. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 1-200% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 5-150% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 25-100% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 15-50% by weight relative to the amount of depolymerized liquids derived from the solid
polymeric material. Tn some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 1-20% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 1-10% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material. In some embodiments, the amount of depolymerized liquids derived from other organic feedstocks added ranges from about 2-6% by weight relative to the amount of depolymerized liquids derived from the solid polymeric material.
[0017] The depolymerization can be a purely thermal reaction or it can employ catalysts. Depending on the starting material and the desired end-product, depolymerization could be employed for a slight or extreme reduction of the molecular weight of the starting material. In some embodiments the depolymerization process preferably employs a catalyst. The preferred catalyst employs a biochar derived from biomass, an activated carbon material, a metal or metal oxide material, or a zeolite or alumina material. Biochar catalysts are particularly inexpensive and, at the end of their usefulness as catalysts, may be utilized as a component of the modified asphalt blend. Zeolite, metal oxide, or alumina catalysts offer high catalytic efficiencies and can be readily regenerated via calcination at high temperatures but are more expensive than biochar materials. In some embodiments of the present invention, certain components within the waste plastics or mixtures of waste plastics may act as catalysts or may generate catalytic species during pyrolysis. For example, chlorinated plastics, such as PVC, or chlorinated additives may generate chlorine radicals during pyrolysis which may promote a catalytic effect on the pyrolysis of other plastic materials or organic feedstocks that may be present. Mixtures of these various catalysts may also be utilized, along with reaction parameters such as temperature, reaction time, and condensation temperature to fine-tune the properties of the resulting depolymerization liquids.
[0018] In some embodiments of the present invention, the combination of other organic feedstocks with the polymeric materials will generate a positive synergistic depolymerization environment requiring lower depolymerization temperatures and, therefore, less energy consumption. In some embodiments, the synergistic effects of the other organic feedstocks may
reduce or even eliminate the need for a depolymerization catalyst to achieve a liquid product with a particular set of properties such as molecular weight, polar content, viscosity, etc.
[0019] In some embodiments, the vaporization process and depolymerization process employs two separate reactors. One or more of the reactors can include a static mixer. An inert gas such as nitrogen can be used to purge oxygen from the reactor and to carry the feedstock vapor from the vaporization reactor to the depolymerization reactor. In some embodiments of the present invention, an applied vacuum is utilized to purge oxygen from the reactor and to pull the feedstock vapor from the vaporization reactor to the depolymerization reactor. Tn some embodiments, the vaporization process and the depolymerization process may occur within a single reactor. In some embodiments, the vaporization and depolymerization temperatures are the same. In some embodiments, the vaporization and depolymerization temperatures may be different.
[0020] Temperatures greater than about 250°C are generally required to effect vaporization, depending on the composition of the feedstock. In some embodiments, vaporization temperatures such as 250-300°C , 3OO-35O°C, 350-400°C, 450-500°C, 500-550°C, 550-600°C, 600-650°C, 650-700°C, 300-400°C, 400-500°C, 500-600°C, or 600-700°C might be utilized. In some embodiments, vaporization temperatures are between 250-400°C. In some embodiments, vaporization temperatures are between 400-500°C. In some embodiments, vaporization temperatures are between 450-550°C. In some embodiments, vaporization temperatures are between 500-600°C. Temperatures greater than about 250°C are generally desired to effect the thermal depolymerization process, depending on the composition of the feedstock and/or catalyst. In some embodiments, depolymerization temperatures such as 250-300°C , 3OO-35O°C, 350-400°C, 450-500°C, 500-550°C, 550-600°C, 600-650°C, 650-700°C, 300-400°C, 400-500°C, 500-600°C, or 600-700°C might be utilized. In some embodiments, depolymerization temperatures are between 400-500°C. In some embodiments, depolymerization temperatures are between 450-550°C. In some embodiments, depolymerization temperatures are between 500- 600°C. In some embodiments, depolymerization temperatures are between 550-650°C. In some embodiments, depolymerization temperatures are between 600-700°C.
[0021] The depolymerization process converts the solid polymeric material, alone or in combination with one or more other organic feedstocks, into a mixture of gaseous, liquid, and solid or wax fractions. The proportion of these different components vary with reaction conditions such as reaction temperature, reaction time, and choice of catalyst (including no catalyst). In some embodiments, it is desirable to minimize the amount of the solid or wax fraction by utilizing higher reaction temperatures. Proper choice of catalyst and a reduced reaction time may also decrease wax yield. In some embodiments, it is desirable to maximize the content of aromatic species in the liquid fraction. Proper choice of catalyst and temperature (higher temperatures, especially temperatures over about 550°C generally favor aromatic production) may also increase the yield of aromatics in the liquid fraction. In some embodiments, it is desirable to maximize the content of aliphatic species in the liquid fraction. In some embodiments, it is desirable to have a certain ratio of aromatic species and aliphatic species in the liquid fraction.
[0022] The depolymerization process generally produces a significant amount of gaseous products, especially under conditions intended to minimize wax formation. Wax products are less desirable products because they require further processing steps (e.g., grinding, pelletizing, prilling, etc.) to be easily handled and require higher blending temperatures when mixed with asphalt binder. Depolymerization conditions favoring low wax also produce higher amounts of aromatics and other unsaturated carbon containing products with concomitant hydrogen gas production. Liquid depolymerization products can be better utilized, and help to lower mixing temperatures, in WMA formulations and can help to soften HMA formulations, making them more ductile. In some embodiments, it may be desirable to collect and utilize the gaseous fraction, possibly including some of the liquid fraction, as fuel to generate the heat required for the vaporization and/or depolymerization reactor(s). In particular, the hydrogen produced during depolymerization is a clean burning fuel that does not contribute to carbon emissions.
[0023] In some embodiments, a typical molecule in the depolymerized liquid material comprises aromatic rings interconnected with one another directly and/or aromatic rings connected by aliphatic species. In some embodiments, the preferred ring count is about 2-6. In some embodiments, the preferred ring count is about 2-5. In some embodiments, the preferred ring count is about 2-4. In some embodiments, the depolymerized liquid material should contain a
small percentage of polar oxygen-containing and/or nitrogen-containing compounds, such as esters, phenolic compounds, and derivatives thereof. In some embodiments, the total heterogeneous element (O, N) in the oil shall be in the range of 1-5% by weight. In some embodiments, the total heterogeneous element (O, N) in the oil shall be in the range of 1-10% by weight. In some embodiments, the total heterogeneous element (O, N) in the oil shall be in the range of 2-6% by weight.
[0024] The depolymerized liquid fraction is generally collected by condensation from the depolymerized vapor stream exiting the reactor(s). A single liquid fraction may be obtained by passing the vapor stream through a single condenser set to a sufficiently low temperature to condense a liquid over a desired molecular weight or carbon (Cn) number. In embodiments of the present invention utilizing an applied vacuum instead of an inert gas purge, lower condenser temperatures will generally be required to condense a liquid of a particular molecular weight or Cn range. Alternatively, multiple fractions of varying molecular weight may be obtained by passing through a series of condensers at sequentially lower temperatures as described above. Any particular depolymerized liquid material fraction may also be further fractionated in a separate step by fractional distillation.
[0025] The present method involves two main concepts: (1) the creation of depolymerized liquid materials via depolymerization of solid plastic materials and/or other organic compounds, and (2) adding these liquids, or a mixture of these liquids, to modify various asphalt compositions. In some embodiments, the depolymerized liquid modifier(s) can be added during a “wet process” to the asphalt binder, i.e., prior to adding aggregates to the asphalt mixture to produce, for example but not limited to, an improved asphalt binder composition. In some embodiments, the depolymerized liquid modifier(s) can be added during a “dry process,” i.e., in concurrence with aggregate, RAP, and/or other solid fdler addition. A non-limiting example of a dry process is shown in FIG. 2. Depolymerization liquid(s) derived from depolymerization of plastics (7) and/or from depolymerization of other organic compounds (8) are mixed with asphalt binder (9), other common asphalt modifiers (10), and solid fillers such as aggregate (11) and/or RAP (12) at approximately 110-160°C to produce the final asphalt concrete formulation (14). In some embodiments, the depolymerized liquid modifier(s) can be sprayed on the RAP content prior to mixing the RAP with a virgin asphalt binder.
[0026] In some embodiments, ground or shredded waste plastic material, which may be the same as or different from the plastic material employed to produce the depolymerization liquid, may be added as a fdler to produce a polymer modified asphalt. In some embodiments, SBS and/or crumb rubber can be ground up or partially depolymerized in a similar depolymerization process and blended in along with the liquid. In some embodiments, ground, crushed or shredded RAP and/or recycled asphalt shingle (RAS) may be added to produce a modified asphalt concrete mixture. In some embodiments, moderate blending temperatures of 100-130°C can be achieved by treating the asphalt binder with the depolymerization liquid prior to adding in aggregates (the liquid can be used as a softening agent for the asphalt binder allowing a WMA process). In some embodiments, the asphalt product can be further modified by materials such as an elastomer, plastomer, wax, poly phosphoric acid, sulfuric acids, amines, amide-diamine, phosphate esters, hydrolene aromatic oils, extender oils, vegetable oils, asphalt sand, naturally occurring bitumens and/or a combination thereof. In some embodiments, the modified asphalt product can be subjected to an emulsifying process by mixing in an emulsifier and water.
[0027] In some embodiments, the addition of the depolymerized liquid improves the processing and physical characteristics of the modified asphalt, including reduction in blend time and/or blend temperature to achieve optimal or near-optimal dispersion of the polymer fillers and/or dispersion of additional modifier(s), resulting in higher throughputs; enablement of higher RAP and RAS loading through reduced mix stiffness and increased ductility; and compaction and material handling. Furthermore, without wishing to be bound by theory, it is believed that modifiers with high aromatic content and/or polar functional groups such as, for example, phenolics and/or amide groups, are particularly effective in deagglomeration of asphaltene sheets present in asphalt materials, while aliphatics and saturated species are effective in softening asphalt binder during blending, and contribute to rutting resistance once applied, hence liquid with aliphatic species can be blended in as an additive to lower the viscosity of asphalt binder during the WMA process. In some embodiments, the liquid modifiers may incorporate 2-40% by weight of depolymerization liquids derived from organic compounds as such liquids contain enhanced amounts of polar functional groups that can facilitate deagglomeration of asphaltene sheets in asphalt formulations. In some embodiments, the depolymerization liquids derived from plastic materials, alone or in conjunction with liquids with polar functional groups, will contain small aromatic compounds along with some amount of saturated and unsaturated aliphatic
compounds which may aid in dispersing and stabilizing the detangled asphaltene sheets present in a solution.
[0028] In other or the same embodiments, the addition of depolymerized liquids improves the physical characteristics of the final asphalt product. The resulting final products can have various properties that differ from their unmodified forms. In some embodiments, the properties include, among other things, improved rutting susceptibility; improved fatigue cracking resistance; improved thermal cracking resistance; improved thermal stability; improved polymer dispersion and viscosity. Improvements to elastomeric properties and energy of deformation are also observed in some embodiments.
[0029] The said depolymerization process yields an additive with significant carbon footprint reduction in the following ways:
(a) It utilizes waste plastics as feedstock which stops said materials from being incinerated.
(b) The depolymerization process can be self-fueling and does not require external energy. The gaseous product in the depolymerization process in general provides adequate heating energy to self-fuel the ongoing said process. In addition, it is possible to optimize hydrogen in the gaseous product by keeping reaction temperatures in an desired range in a catalytic reaction, hence emitting mostly H2O as steam (90%+ hydrogen by volume in gaseous product is achievable from experimental data).
(c) A negative carbon footprint is achievable with biochar-based catalyst (derived from organic products such as agricultural waste) and/or co-depolymerization with an organic product (such as agricultural waste). CO2 was sequestered during the growth of the organic product, when used to produce biochar and/or co-depolymerization the originally sequestered carbon is locked in solid phase and/or liquid phase. For example, in the case of biochar once its catalytic uses are finished, such biochar solid is added into asphalt mixture as a filler, eventually locking up the sequestered CO2. With a typical catalyst to feedstock ratio, the carbon footprint of the depolymerized product is further offset and
achieves carbon neutrality, yielding 1 .6 metric tons of CO2 captured from the environment for each ton of waste plastics depolymerized.
(d) When considering that such waste plastic material is likely to be incinerated otherwise (at an average of 2.9 ton CO2 emission / ton of plastic), the carbon emission reduction is much more significant, which means for each ton of plastic waste utilized in said depolymerization process 4.5 tons of CO2 emissions is offset.
(e) When such depolymerized product is applied to replace current popular commercial additives, the carbon footprint to produce such additives is further offset. For example, to produce 1 ton of RAP and WMA asphalt pavement mixture (at 50% RAP content), an average of 3.43 kg CO2 is emitted from production of conventional additives. With a 5% asphalt binder dosage, the use of the depolymerized liquid additives of the present invention eliminates the above said emissions and contributes an effective negative 4.43 kg CO2 - hence a total of 7.86 kg carbon footprint reduction for each ton of pavement constructed. This means there is potential to reduce the paving greenhouse gas (GHG) emissions by 48%. With a higher RAP content of 93%, the GHG emissions are further reduced by 84%, resulting in a CO2 reduction of 35 metric tons in the US alone and an estimated 180 metric tons globally.
EXAMPLES
[0030] In the following examples, efforts have been made to ensure accuracy with respect to numbers used (e.g., amounts, temperature, etc.) but some experimental error and deviation should be accounted for. The examples are to be considered as not being limiting of the invention described herein.
General Procedures:
[0031] Ground almond shell (AS) was obtained from Northern California almond farms. Representative waste plastic materials were obtained from three different types of yoga mat products:
(i) YM-1 was a yoga mat comprising polyester and natural rubber;
(ii) YM-2 was a multilayered yoga mat comprising various plastics along with natural and synthetic rubbers; and
(iii) YM-3 was a yoga mat comprising polyvinyl chloride (PVC) and associated ester- based plasticizers.
All pyrolysis reactions were performed in a glass tube placed into a tube furnace with an inert gas purge or held under a vacuum (similar results were obtained). A section near one end of the glass tube was plugged with glass wool and an amount of one or more waste plastic material along with any catalyst, if used, was loaded into the tube. Another glass wool plug was inserted above the material to hold it in place. The end of the tube was connected to a condenser cooled to a temperature of about 10°C. The tube with the plastic material was loaded into a tube furnace and rapidly heated to the desired pyrolysis temperature. The resulting cracked products were then carried by the purge gas stream or applied vacuum through the condenser where hydrocarbons of approximately C?-Cs and greater were condensed out as liquids. Hydrocarbon products lighter than about C?-Cs passed through the condenser, and some amount of solid residue remained in the tube.
Example 1 Pyrolysis of Mixed Waste Plastics at Different Temperatures
[0032] Representative mixed waste plastic materials YM-1 and YM-2 were pyrolyzed according to the general procedure described above at different pyrolysis temperatures (400°C, 450°C, and 500°C) to yield the mix of depolymerized liquid, solid residue, and gas products as shown in Table 1 and represented graphically in FIG. 3. All of the values shown are an average of three runs. Generally, higher pyrolysis temperatures yielded higher depolymerized liquid and gas yields and reduced residual solid yields.
Example 2
Co-Pyrolysis of Waste Materials with PVC
[0033] The various waste materials YM-1, YM-2, and AS were pyrolyzed or co-pyrolyzed with YM-3 (comprising PVC) at 400°C according to the general procedure described above to yield the mix of liquid, solid, and gas products as shown in Table 2 and graphically illustrated in FIG.
4 (YM-1 /YM-3), FIG. 5 (YM-2/YM-3), and FIG. 6 (AS/YM-3). All of the values shown are an average of three runs. When waste plastics (YM-1 or YM-2) or organic feedstock (AS) were co- pyrolyzed with the PVC-containing material (YM-3), higher yields of liquid product were observed than were predicted based on pyrolysis yields of the individual materials as shown in Table 3.
Example 3 Rejuvenation Performance of Depolymerized Liquids from Waste Plastics
[0034] A depolymerization liquid was prepared by the co-pyrolysis of 1 : 1 YM-l/YM-3 at 400°C according to the general procedure as in Run 9 of Example 2 above. A sample of “aged” asphalt binder was prepared from a virgin bitumen material (“Virgin”) via standard laboratory accelerated aging procedures in a rolling thin film oven pressure vessel to a 10-year field aged equivalent material (“Aged”). Samples of rejuvenated asphalt binder were prepared by blending the aged bitumen material with (i) 10% by weight of the inventive depolymerization liquid (“Rejuvenated (I)”) and (ii) 10% by weight of a standard commercial rejuvenating material Reclamite® (Tricor Refining, LLC) (“Rejuvenated (R)") as a reference material. Standard linear amplitude sweep (LAS) testing method AASHTO T 391-20 was run (FIG. 7) to determine the various asphalt binders' resistance to fatigue damage by means of cyclic loading employing systematic, linearly increasing load amplitudes. This test is commonly used to simulate field durability. Generally speaking, the LAS curves of each binder give a visual estimate of the load bearing performance when compared to one another. An ideal binder's modulus (y axis) should stay relatively stable across all levels of deformation. However, in reality, a binder will often yield with a sudden decrease of modulus, which is generally ascribed to development of significant cracks in the testing material. As seen in FIG. 7, the virgin asphalt binder (Virgin) did not yield during testing and had a softer modulus in general. The curve for the Aged material, which would be highly oxidized, shows a much higher modulus (stiffer material) that yields early on during the LAS testing as the material cracks. The curves for the rejuvenated samples prepared from the depolymerization liquid of the present invention, Rejuvenated (I), and from the reference commercial material, Rejuvenated (R), both show good performance. In fact, in terms of reducing the aged binder modulus and increasing flexibility, the inventive depolymerization liquid out-performed the commercial product.
INDUSTRIAL APPLICABILITY
[0035] This invention may be industrially applied to the development, manufacture, and use of an asphalt modifier that is environmentally friendly with low greenhouse gas (GHG), produced by using solid plastic materials, alone or in conjunction with other organic feedstocks, to prepare carbon-efficient asphalt formulations and end-products.
Claims
1. A method for forming an asphalt modifier comprising a depolymerized liquid material, the method comprising:
(a) selecting a solid polymeric material, or a mixture of solid polymeric materials;
(b) heating the solid polymeric material or mixture of solid polymeric materials in a vaporization reactor at a vaporization temperature under an inert gas stream or an applied vacuum such that the solid polymeric material or mixture of solid polymeric materials turns into a vaporized material;
(c) transporting the vaporized material with the inert gas stream or the vacuum environment to a depolymerization reactor at a depolymerization temperature sufficient to effect a thermal depolymerization reaction of the vaporized material and form a depolymerized vapor stream comprising a mixture of depolymerization products; and
(d) transporting the depolymerized vapor stream through a condenser at a lower temperature, or through a series of condensers at sequentially lower temperatures, to produce one or more depolymerized liquid materials and a gaseous product stream.
2. The method of claim 1 , wherein a catalyst is utilized to facilitate the thermal depolymerization reaction.
3. The method of claim 2, wherein the catalyst comprises a zeolite or alumina.
4. The method of claim 2, wherein the catalyst comprises biochar derived from biomass.
5. The method of claim 2, wherein the catalyst comprises activated carbon.
6. The method of claim 2, wherein the catalyst comprises a metal or metal oxide or a combination thereof.
7. The method as in any of claims 1-6, wherein the depolymerization temperature is greater
than 550°C and a typical molecule in the depolymerized liquid material comprises aromatic rings interconnected with one another directly and/or aromatic rings connected by aliphatic species. The method as in any of claims 1-6, wherein said depolymerization process further employs a fractionation method. The method of claim 8, wherein the fractionation method employs heating the mixture. The method of claim 8, wherein the fractionation method employs solvent. The method as in any of claims 1-6, wherein the vaporization reactor and the depolymerization reactor are a single reaction chamber. The method as in any of claims 1-6, wherein the vaporization temperature and the depolymerization temperature are different. The method as in any of claims 1-6, wherein the vaporization temperature and the depolymerization temperature are the same. The method as in any of claims 1-6, wherein the solid polymeric materials comprise waste plastics or a mixture of waste plastics. The method as in any of claims 1-6, wherein other organic materials are combined with the solid polymeric material or mixture of solid polymeric materials. The method as in claim 15, wherein the depolymerized liquid material contains polar oxygen-containing and/or nitrogen-containing compounds. A method for forming an asphalt modifier comprising a depolymerized liquid material, the method comprising:
(a) selecting an organic material, or a mixture of organic materials;
(b) heating the organic material or mixture of organic materials in a vaporization reactor at a vaporization temperature under an inert gas environment or a vacuum environment such that the organic material or mixture of organic materials turns into a vaporized material;
(c) transporting the vaporized material with the inert gas to a depolymerization reactor at a depolymerization temperature sufficient to effect a thermal depolymerization reaction of the vaporized material and form a depolymerized vapor stream comprising a mixture of depolymerization products; and
(d) transporting the depolymerized vapor stream through a condenser at a lower temperature, or through a series of condensers at sequentially lower temperatures, to produce one or more depolymerized liquid materials and a gaseous product stream. The asphalt modifier of any of claims 1-6. The asphalt modifier of claim 7. The asphalt modifier of claim 16. The asphalt modifier of claim 17. The asphalt modifier of claim 18 further compromising an additive selected from the group consisting of an elastomer, plastomer, wax, poly phosphoric acid, sulfuric acids, amines, amide-diamine, phosphate esters, hydrolene aromatic oil, extender oils, vegetable oils, rerefined motor oil bottoms, asphalt sand, bio-based oils, pyrolytic rubber oil or wax, aromatic extract, naturally occurring bitumens or combinations thereof. The asphalt modifier of claim 19 further compromising an additive selected from the group consisting of an elastomer, plastomer, wax, poly phosphoric acid, sulfuric acids, amines, amide-diamine, phosphate esters, hydrolene aromatic oil, extender oils, vegetable oils, rerefined motor oil bottoms, asphalt sand, bio-based oils, pyrolytic rubber oil or wax,
aromatic extract, naturally occurring bitumens or combinations thereof. The asphalt modifier of claim 20 further compromising an additive selected from the group consisting of an elastomer, plastomer, wax, poly phosphoric acid, sulfuric acids, amines, amide-diamine, phosphate esters, hydrolene aromatic oil, extender oils, vegetable oils, rerefined motor oil bottoms, asphalt sand, bio-based oils, pyrolytic rubber oil or wax, aromatic extract, naturally occurring bitumens or combinations thereof. The asphalt modifier of claim 21 further compromising an additive selected from the group consisting of an elastomer, plastomer, wax, poly phosphoric acid, sulfuric acids, amines, amide-diamine, phosphate esters, hydrolene aromatic oil, extender oils, vegetable oils, rerefined motor oil bottoms, asphalt sand, bio-based oils, pyrolytic rubber oil or wax, aromatic extract, naturally occurring bitumens or combinations thereof. The asphalt modifier of claim 16, added to an asphalt binder to produce a modified asphalt binder. The asphalt modifier of claim 16, added to an asphalt concrete mixture to produce a modified asphalt concrete mixture. The asphalt modifier of claim 16, added to a recycled or partially recycled asphalt concrete mixture to produce a modified asphalt concrete mixture. The asphalt modifier of claim 16 further compromising an emulsifier and water to produce an emulsified mixture used as asphalt pavement surface treatment. The asphalt modifier of claim 17, added to an asphalt binder to produce a modified asphalt binder. The asphalt modifier of claim 17, added to an asphalt concrete mixture to produce a modified asphalt concrete mixture.
The asphalt modifier of claim 17, added to a recycled or partially recycled asphalt concrete mixture to produce a modified asphalt concrete mixture. The asphalt modifier of claim 17 further compromising an emulsifier and water to produce an emulsified mixture used as asphalt pavement surface treatment. A method to rejuvenate a RAP material comprising treating the RAP material with the asphalt modifier of claim 16. A method to rejuvenate a RAP material comprising treating the RAP material with the asphalt modifier of claim 17. The method as in any of claims 1-6 wherein the gaseous product stream is utilized as fuel to heat the vaporization reactor and/or the depolymerization reactor. A method for producing a modified asphalt binder comprising mixing asphalt binder with the asphalt modifier of claim 16 in a wet process. A method for producing a modified asphalt binder comprising mixing asphalt binder with the asphalt modifier of claim 17 in a wet process. A method for producing an asphalt concrete mixture comprising mixing asphalt binder, the asphalt modifier of claim 16, and one or more filler materials selected from the group consisting of aggregate, RAP, and RAS in a dry process. A method for producing an asphalt concrete mixture comprising mixing asphalt binder, the asphalt modifier of claim 17, and one or more filler materials selected from the group consisting of aggregate, RAP, and RAS in a dry process.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US202263390930P | 2022-07-20 | 2022-07-20 | |
US63/390,930 | 2022-07-20 |
Publications (2)
Publication Number | Publication Date |
---|---|
WO2024020510A2 true WO2024020510A2 (en) | 2024-01-25 |
WO2024020510A3 WO2024020510A3 (en) | 2024-03-07 |
Family
ID=89618516
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/US2023/070632 WO2024020510A2 (en) | 2022-07-20 | 2023-07-20 | Methods for modifying asphalt using low greenhouse gas liquids obtained from depolymerization of waste plastics |
Country Status (1)
Country | Link |
---|---|
WO (1) | WO2024020510A2 (en) |
Family Cites Families (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TW200732467A (en) * | 2005-09-28 | 2007-09-01 | Cwt Llc Ab | Process for conversion of organic, waste, or low-value materials into useful products |
US7638040B2 (en) * | 2007-06-29 | 2009-12-29 | Uop Llc | Process for upgrading contaminated hydrocarbons |
US8471079B2 (en) * | 2008-12-16 | 2013-06-25 | Uop Llc | Production of fuel from co-processing multiple renewable feedstocks |
US8696806B2 (en) * | 2009-05-01 | 2014-04-15 | Iowa State University Research Foundation, Inc. | Asphalt materials containing bio-oil and methods for production thereof |
EP2970039A4 (en) * | 2013-03-15 | 2016-10-26 | Pinova Inc | Asphalt emulsifiers derived from pyrolyzed wood |
US9546275B2 (en) * | 2013-04-09 | 2017-01-17 | Saudi Arabian Oil Company | Enhancing properties of sulfur extended asphalt using polyethylene wax |
US10570286B2 (en) * | 2016-08-30 | 2020-02-25 | Iowa State University Research Foundation, Inc. | Asphalt products and methods of producing them for rejuvenation and softening of asphalt |
LT3555231T (en) * | 2016-12-14 | 2023-08-25 | Mura Technology Limited | Method for producing biofuel by converting a polymeric material melt mixed with supercrital water |
TWI830098B (en) * | 2020-12-22 | 2024-01-21 | 義大利商巴塞爾聚烯烴義大利股份有限公司 | Process for the depolymerization of plastic waste material |
-
2023
- 2023-07-20 WO PCT/US2023/070632 patent/WO2024020510A2/en unknown
Also Published As
Publication number | Publication date |
---|---|
WO2024020510A3 (en) | 2024-03-07 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US11155696B2 (en) | Preparation and uses of bio-adhesives | |
Aziz et al. | An overview on alternative binders for flexible pavement | |
US8758597B2 (en) | Reclaimed asphalt pavement | |
Raman et al. | A review on the application of bio-oil as an additive for asphalt | |
WO2009042675A1 (en) | Incorporation of heat-treated recycled tire rubber in asphalt compositions | |
CN107849467A (en) | For the enhancing solvent deasphalting and coking method of the integration for producing oil green coke | |
US20200291234A1 (en) | Waste tire-derived asphalt modifier | |
US11193243B2 (en) | Agricultural oil-based sealing and preservation agent and method of treating asphalt construction or pavement | |
US9593211B2 (en) | Asphalt binder modifier composition | |
US4278469A (en) | Process for repairing asphalt pavement | |
US4358554A (en) | Process for repairing asphalt pavement | |
WO2024020510A2 (en) | Methods for modifying asphalt using low greenhouse gas liquids obtained from depolymerization of waste plastics | |
US11459274B2 (en) | System and method for generating tire rubber asphalt | |
CN105885151A (en) | Normal-temperature regenerating agent for asphalt mixtures and method for manufacturing normal-temperature regenerating agent | |
Mousavi et al. | Preventing emissions of hazardous organic compounds from bituminous composites | |
Tosun | Production and characterisation of waste tire pyrolytic oil–Investigating physical and rheological behaviour of pyrolytic oil modified asphalt binder | |
US20220243066A1 (en) | Upgrading asphalt by incorporation of bio-oils | |
CN1939975A (en) | Asphalt road surface functional repairing agent and its production | |
CN112745690B (en) | Biomass heavy oil modified asphalt material and preparation thereof | |
Williams et al. | Development of non-petroleum-based binders for use in flexible pavements–Phase II | |
RU2752591C1 (en) | Method for producing road bitumen | |
Bolakar Tosun | Production and characterisation of waste tire pyrolytic oil–Investigating physical and rheological behaviour of pyrolytic oil modified asphalt binder | |
Phase | Development of Non-Petroleum-Based Binders for Use in Flexible Pavements–Phase II | |
CN112126238A (en) | Asphalt mixture modifier prepared from coal tar and preparation method thereof | |
Roy et al. | Oil and carbon black by pyrolysis of used tires |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 23843898 Country of ref document: EP Kind code of ref document: A2 |