JP2000219884A - Conversion of plastic waste to fuel oil - Google Patents
Conversion of plastic waste to fuel oilInfo
- Publication number
- JP2000219884A JP2000219884A JP2534099A JP2534099A JP2000219884A JP 2000219884 A JP2000219884 A JP 2000219884A JP 2534099 A JP2534099 A JP 2534099A JP 2534099 A JP2534099 A JP 2534099A JP 2000219884 A JP2000219884 A JP 2000219884A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- clay mineral
- fuel oil
- acid
- reaction
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000000295 fuel oil Substances 0.000 title claims abstract description 25
- 238000006243 chemical reaction Methods 0.000 title claims description 90
- 239000013502 plastic waste Substances 0.000 title abstract 3
- 239000003054 catalyst Substances 0.000 claims abstract description 63
- 239000002734 clay mineral Substances 0.000 claims abstract description 45
- 239000004033 plastic Substances 0.000 claims abstract description 37
- 229920003023 plastic Polymers 0.000 claims abstract description 37
- 239000002699 waste material Substances 0.000 claims abstract description 26
- 238000000034 method Methods 0.000 claims abstract description 23
- 239000003921 oil Substances 0.000 claims description 32
- 239000001257 hydrogen Substances 0.000 claims description 24
- 229910052739 hydrogen Inorganic materials 0.000 claims description 24
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 22
- 239000002253 acid Substances 0.000 claims description 18
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 14
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 10
- 239000010949 copper Substances 0.000 claims description 10
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims description 9
- 229910052802 copper Inorganic materials 0.000 claims description 9
- 150000002500 ions Chemical class 0.000 claims description 8
- 239000000203 mixture Substances 0.000 claims description 8
- 150000001768 cations Chemical class 0.000 claims description 7
- 229930195733 hydrocarbon Natural products 0.000 claims description 7
- 150000002430 hydrocarbons Chemical class 0.000 claims description 7
- 229910052751 metal Inorganic materials 0.000 claims description 7
- 239000002184 metal Substances 0.000 claims description 7
- WGLPBDUCMAPZCE-UHFFFAOYSA-N Trioxochromium Chemical group O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 claims description 6
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 6
- 229910044991 metal oxide Inorganic materials 0.000 claims description 6
- 150000004706 metal oxides Chemical class 0.000 claims description 6
- 229910052759 nickel Inorganic materials 0.000 claims description 6
- 239000011701 zinc Substances 0.000 claims description 6
- 229910000423 chromium oxide Inorganic materials 0.000 claims description 5
- 229910052725 zinc Inorganic materials 0.000 claims description 5
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 4
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 4
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 4
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims description 2
- 229910017604 nitric acid Inorganic materials 0.000 claims description 2
- 229910052761 rare earth metal Inorganic materials 0.000 claims description 2
- 229910052625 palygorskite Inorganic materials 0.000 abstract description 16
- GUJOJGAPFQRJSV-UHFFFAOYSA-N dialuminum;dioxosilane;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3].O=[Si]=O.O=[Si]=O.O=[Si]=O.O=[Si]=O GUJOJGAPFQRJSV-UHFFFAOYSA-N 0.000 abstract description 5
- 229910052901 montmorillonite Inorganic materials 0.000 abstract description 5
- HPTYUNKZVDYXLP-UHFFFAOYSA-N aluminum;trihydroxy(trihydroxysilyloxy)silane;hydrate Chemical compound O.[Al].[Al].O[Si](O)(O)O[Si](O)(O)O HPTYUNKZVDYXLP-UHFFFAOYSA-N 0.000 abstract description 3
- 229910001919 chlorite Inorganic materials 0.000 abstract description 3
- 229910052619 chlorite group Inorganic materials 0.000 abstract description 3
- QBWCMBCROVPCKQ-UHFFFAOYSA-N chlorous acid Chemical compound OCl=O QBWCMBCROVPCKQ-UHFFFAOYSA-N 0.000 abstract description 3
- 229910052621 halloysite Inorganic materials 0.000 abstract description 3
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 abstract description 3
- 229910052622 kaolinite Inorganic materials 0.000 abstract description 3
- 229910052620 chrysotile Inorganic materials 0.000 abstract description 2
- 229910052899 lizardite Inorganic materials 0.000 abstract description 2
- IBPRKWGSNXMCOI-UHFFFAOYSA-N trimagnesium;disilicate;hydrate Chemical compound O.[Mg+2].[Mg+2].[Mg+2].[O-][Si]([O-])([O-])[O-].[O-][Si]([O-])([O-])[O-] IBPRKWGSNXMCOI-UHFFFAOYSA-N 0.000 abstract description 2
- CWBIFDGMOSWLRQ-UHFFFAOYSA-N trimagnesium;hydroxy(trioxido)silane;hydrate Chemical compound O.[Mg+2].[Mg+2].[Mg+2].O[Si]([O-])([O-])[O-].O[Si]([O-])([O-])[O-] CWBIFDGMOSWLRQ-UHFFFAOYSA-N 0.000 abstract description 2
- 229910052902 vermiculite Inorganic materials 0.000 abstract description 2
- 239000010455 vermiculite Substances 0.000 abstract description 2
- 235000019354 vermiculite Nutrition 0.000 abstract description 2
- FBPFZTCFMRRESA-FSIIMWSLSA-N L-glucitol Chemical compound OC[C@H](O)[C@H](O)[C@@H](O)[C@H](O)CO FBPFZTCFMRRESA-FSIIMWSLSA-N 0.000 abstract 1
- 229910052898 antigorite Inorganic materials 0.000 abstract 1
- VNSBYDPZHCQWNB-UHFFFAOYSA-N calcium;aluminum;dioxido(oxo)silane;sodium;hydrate Chemical compound O.[Na].[Al].[Ca+2].[O-][Si]([O-])=O VNSBYDPZHCQWNB-UHFFFAOYSA-N 0.000 abstract 1
- 229910001649 dickite Inorganic materials 0.000 abstract 1
- 229910052631 glauconite Inorganic materials 0.000 abstract 1
- 239000000047 product Substances 0.000 description 41
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 30
- 229910052799 carbon Inorganic materials 0.000 description 25
- 239000004698 Polyethylene Substances 0.000 description 22
- 239000012263 liquid product Substances 0.000 description 20
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 17
- 239000004927 clay Substances 0.000 description 16
- -1 polyethylene Polymers 0.000 description 16
- 239000004743 Polypropylene Substances 0.000 description 13
- 238000000354 decomposition reaction Methods 0.000 description 13
- 239000007789 gas Substances 0.000 description 13
- 229910052757 nitrogen Inorganic materials 0.000 description 13
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 10
- 238000005984 hydrogenation reaction Methods 0.000 description 9
- 239000007788 liquid Substances 0.000 description 9
- 239000012188 paraffin wax Substances 0.000 description 9
- XLOMVQKBTHCTTD-UHFFFAOYSA-N zinc oxide Inorganic materials [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 description 9
- 150000001336 alkenes Chemical class 0.000 description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- 229910001868 water Inorganic materials 0.000 description 7
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 6
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 6
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 description 6
- 229920000573 polyethylene Polymers 0.000 description 6
- 239000007864 aqueous solution Substances 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- JRZJOMJEPLMPRA-UHFFFAOYSA-N olefin Natural products CCCCCCCC=C JRZJOMJEPLMPRA-UHFFFAOYSA-N 0.000 description 5
- 229920001155 polypropylene Polymers 0.000 description 5
- 239000000243 solution Substances 0.000 description 5
- 238000005979 thermal decomposition reaction Methods 0.000 description 5
- 239000004215 Carbon black (E152) Substances 0.000 description 4
- 239000004113 Sepiolite Substances 0.000 description 4
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 4
- 238000005336 cracking Methods 0.000 description 4
- 229910001873 dinitrogen Inorganic materials 0.000 description 4
- 229910052624 sepiolite Inorganic materials 0.000 description 4
- 235000019355 sepiolite Nutrition 0.000 description 4
- 239000000377 silicon dioxide Substances 0.000 description 4
- 239000011787 zinc oxide Substances 0.000 description 4
- 150000001342 alkaline earth metals Chemical class 0.000 description 3
- 238000004523 catalytic cracking Methods 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 229910052500 inorganic mineral Inorganic materials 0.000 description 3
- 150000002739 metals Chemical class 0.000 description 3
- 239000011707 mineral Substances 0.000 description 3
- 229910000480 nickel oxide Inorganic materials 0.000 description 3
- 229920002620 polyvinyl fluoride Polymers 0.000 description 3
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 239000004793 Polystyrene Substances 0.000 description 2
- 230000002378 acidificating effect Effects 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 229910052782 aluminium Inorganic materials 0.000 description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 150000001491 aromatic compounds Chemical class 0.000 description 2
- 239000000292 calcium oxide Substances 0.000 description 2
- 125000004432 carbon atom Chemical group C* 0.000 description 2
- 238000005341 cation exchange Methods 0.000 description 2
- 229910052804 chromium Inorganic materials 0.000 description 2
- 239000011651 chromium Substances 0.000 description 2
- 229910000431 copper oxide Inorganic materials 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 238000004817 gas chromatography Methods 0.000 description 2
- 150000002431 hydrogen Chemical class 0.000 description 2
- 238000009830 intercalation Methods 0.000 description 2
- 238000006317 isomerization reaction Methods 0.000 description 2
- 229910052746 lanthanum Inorganic materials 0.000 description 2
- GNRSAWUEBMWBQH-UHFFFAOYSA-N oxonickel Chemical compound [Ni]=O GNRSAWUEBMWBQH-UHFFFAOYSA-N 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 229920002223 polystyrene Polymers 0.000 description 2
- 229910052700 potassium Inorganic materials 0.000 description 2
- 239000003507 refrigerant Substances 0.000 description 2
- 229910000275 saponite Inorganic materials 0.000 description 2
- 229910052708 sodium Inorganic materials 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 229920001169 thermoplastic Polymers 0.000 description 2
- VXUYXOFXAQZZMF-UHFFFAOYSA-N titanium(IV) isopropoxide Chemical compound CC(C)O[Ti](OC(C)C)(OC(C)C)OC(C)C VXUYXOFXAQZZMF-UHFFFAOYSA-N 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- 229910018516 Al—O Inorganic materials 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical compound [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 description 1
- 239000005751 Copper oxide Substances 0.000 description 1
- YZCKVEUIGOORGS-OUBTZVSYSA-N Deuterium Chemical compound [2H] YZCKVEUIGOORGS-OUBTZVSYSA-N 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 229910004283 SiO 4 Inorganic materials 0.000 description 1
- PPBRXRYQALVLMV-UHFFFAOYSA-N Styrene Chemical group C=CC1=CC=CC=C1 PPBRXRYQALVLMV-UHFFFAOYSA-N 0.000 description 1
- YZCKVEUIGOORGS-NJFSPNSNSA-N Tritium Chemical compound [3H] YZCKVEUIGOORGS-NJFSPNSNSA-N 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- XHCLAFWTIXFWPH-UHFFFAOYSA-N [O-2].[O-2].[O-2].[O-2].[O-2].[V+5].[V+5] Chemical compound [O-2].[O-2].[O-2].[O-2].[O-2].[V+5].[V+5] XHCLAFWTIXFWPH-UHFFFAOYSA-N 0.000 description 1
- 238000010306 acid treatment Methods 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 229910001583 allophane Inorganic materials 0.000 description 1
- WYTGDNHDOZPMIW-RCBQFDQVSA-N alstonine Natural products C1=CC2=C3C=CC=CC3=NC2=C2N1C[C@H]1[C@H](C)OC=C(C(=O)OC)[C@H]1C2 WYTGDNHDOZPMIW-RCBQFDQVSA-N 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 238000003421 catalytic decomposition reaction Methods 0.000 description 1
- 229940117975 chromium trioxide Drugs 0.000 description 1
- GAMDZJFZMJECOS-UHFFFAOYSA-N chromium(6+);oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[Cr+6] GAMDZJFZMJECOS-UHFFFAOYSA-N 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- CRCKGIUJMFFISH-UHFFFAOYSA-N copper;ethanolate Chemical compound [Cu+2].CC[O-].CC[O-] CRCKGIUJMFFISH-UHFFFAOYSA-N 0.000 description 1
- BCAARMUWIRURQS-UHFFFAOYSA-N dicalcium;oxocalcium;silicate Chemical compound [Ca+2].[Ca+2].[Ca]=O.[O-][Si]([O-])([O-])[O-] BCAARMUWIRURQS-UHFFFAOYSA-N 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 229910000271 hectorite Inorganic materials 0.000 description 1
- KWLMIXQRALPRBC-UHFFFAOYSA-L hectorite Chemical compound [Li+].[OH-].[OH-].[Na+].[Mg+2].O1[Si]2([O-])O[Si]1([O-])O[Si]([O-])(O1)O[Si]1([O-])O2 KWLMIXQRALPRBC-UHFFFAOYSA-L 0.000 description 1
- 239000005457 ice water Substances 0.000 description 1
- 230000002687 intercalation Effects 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- FZLIPJUXYLNCLC-UHFFFAOYSA-N lanthanum atom Chemical compound [La] FZLIPJUXYLNCLC-UHFFFAOYSA-N 0.000 description 1
- 229910001425 magnesium ion Inorganic materials 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 125000002496 methyl group Chemical group [H]C([H])([H])* 0.000 description 1
- 239000010445 mica Substances 0.000 description 1
- 229910052618 mica group Inorganic materials 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 229910000273 nontronite Inorganic materials 0.000 description 1
- CMOAHYOGLLEOGO-UHFFFAOYSA-N oxozirconium;dihydrochloride Chemical compound Cl.Cl.[Zr]=O CMOAHYOGLLEOGO-UHFFFAOYSA-N 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 229910052903 pyrophyllite Inorganic materials 0.000 description 1
- 238000004445 quantitative analysis Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 229910021647 smectite Inorganic materials 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 229910001935 vanadium oxide Inorganic materials 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000001993 wax Substances 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Catalysts (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】この発明は廃プラスチックを
分解して燃料油を得る方法に関する。The present invention relates to a method for obtaining fuel oil by decomposing waste plastic.
【0002】[0002]
【従来の技術】使用済みの廃棄プラスチック(以下、廃
プラスチックと称する。)の処理は今日的な課題であ
る。古くは土中に埋設・廃棄したり、それを燃焼して熱
エネルギーを回収する処理手段しかなかったが、いうま
でもなくこれらの処理手段は環境問題を引き起こすおそ
がある。そこで、これに代わり、現在ではそれを熱分解
して分解生成物として油化物を得る処理手段が提案され
ており、特にポリエチレン、ポリプロピレン、ポリスチ
レンなどの熱可塑性ポリマーに有効な処理手段として注
目されている。2. Description of the Related Art Disposal of used waste plastic (hereinafter referred to as waste plastic) is a present-day problem. In the old days, there were only treatment means for burying and disposing in the soil or burning it to recover thermal energy. Needless to say, these treatment means may cause environmental problems. Therefore, instead of this, at present, processing means for thermally decomposing it to obtain an oily product as a decomposition product has been proposed, and in particular, has been attracting attention as an effective processing means for thermoplastic polymers such as polyethylene, polypropylene, and polystyrene. I have.
【0003】ところで、廃プラスチックの処理にあたっ
てはいうまでもなく経済性も考慮されなければならな
い。上記の熱分解して油化する処理手段においては、分
解生成物として燃料油等を回収してリサイクルが可能な
反面、熱分解のために多大の熱エネルギーを使用しなけ
ればならないという問題点が指摘されている。[0003] In the treatment of waste plastics, it goes without saying that economics must be considered. In the above-mentioned treatment means for thermal decomposition and conversion to oil, fuel oil and the like can be recovered as a decomposition product and recycled, but on the other hand, a large amount of heat energy must be used for thermal decomposition. It is pointed out.
【0004】そのため、反応温度を下げて分解反応のた
めに熱エネルギーを節約すると共に有用な分解生成物を
効率よく回収できることが望まれ、このような目的に沿
う技術として、従来無触媒で熱分解して油化していたこ
とに代わり、触媒を用いて熱分解あるいは水素化する技
術が公知であった。そして、触媒としては、ゼオライ
ト、シリカ・アルミナ、それらに鉄、アルミニウムなど
の金属を添加したものが公知であった。[0004] Therefore, it is desired to reduce the reaction temperature to save thermal energy for the decomposition reaction and to efficiently recover useful decomposition products. Instead of oiling, there has been known a technique of performing thermal decomposition or hydrogenation using a catalyst. As the catalyst, zeolite, silica / alumina, and those obtained by adding metals such as iron and aluminum to them have been known.
【0005】[0005]
【発明が解決しようとする課題】しかしながら、上記の
触媒を用いた熱分解処理も経済性という観点からは未だ
完全なものではなく、より安価な触媒を用いて比較的低
温且つ短時間で廃プラスチックを効率よく分解し、利用
価値の高い燃料油を得られる技術が切望されていた。However, the thermal decomposition treatment using the above-mentioned catalyst is not yet complete from the viewpoint of economy, and waste plastics are produced at a relatively low temperature and in a short time using a less expensive catalyst. There has been a keen need for a technology that can efficiently decompose the oil and obtain fuel oil of high utility value.
【0006】この発明は以上の従来技術の問題点に鑑み
て創作されたものであり、廃プラスチック、主としてポ
リエチレン、ポリプロピレン、ポリスチレンなどの熱可
塑性ポリマーに触媒を用いて、従来の無触媒分解や触媒
分解に比べて短い時間で、しかも低い熱エネルギーで分
解し、使用可能な分解油(主として燃料に使える燃料
油)又はスチレンモノマーとして回収する触媒を提供す
ることを目的とする。The present invention has been made in view of the above-mentioned problems of the prior art, and uses a catalyst for waste plastics, mainly thermoplastic polymers such as polyethylene, polypropylene, and polystyrene, to obtain a conventional catalyst-free decomposition or catalyst. It is an object of the present invention to provide a catalyst that decomposes in a shorter time and with lower thermal energy compared to cracking and recovers it as usable cracked oil (mainly fuel oil usable as fuel) or styrene monomer.
【0007】[0007]
【課題を解決するための手段】すなわち、この発明の廃
プラスチックの燃料油化方法は、廃プラスチックを熱分
解して燃料油を回収するにあたり、粘土鉱物を触媒とし
て用いることを特徴とする。That is, the method for converting waste plastics into fuel oil according to the present invention is characterized in that clay minerals are used as catalysts when recovering fuel oil by thermally decomposing waste plastics.
【0008】この場合、この発明においては触媒として
天然の粘土鉱物をそのまま使用する他、それらを酸で処
理して酸性を持たせたもの、又は粘土鉱物がもつ陽イオ
ン交換性を利用して各種のイオンで交換修飾したもの、
又は粘土鉱物にニッケル、亜鉛、銅、酸化クロム等の金
属ならびに金属酸化物を添加したもの、又は粘土鉱物の
層状構造に基づく層間にジルコニア、銅、チタニア、バ
ナジア等を挿入したもの、又はこれらを組み合わせて活
性を向上させたものを使用することも開示する。In this case, in the present invention, in addition to using natural clay minerals as a catalyst as they are, those obtained by treating them with an acid to make them acidic, or utilizing the cation exchange property of the clay minerals, Exchange-modified with ions of
Or clay minerals added with metals and metal oxides such as nickel, zinc, copper and chromium oxide, or zirconia, copper, titania, vanadia, etc. inserted between layers based on the layered structure of clay minerals, or these Also disclosed is the use of a combination which has improved activity.
【0009】又、熱分解を窒素、又は窒素・水素の混合
ガス気流中で行うことも開示する。It is also disclosed that the pyrolysis is performed in a stream of nitrogen or a mixed gas of nitrogen and hydrogen.
【0010】以上の構成よりなるこの発明の廃プラスチ
ックの燃料油化方法においては、従来の触媒を使用した
場合の分解反応温度である400℃〜500℃と比較し
て低温な約400℃で廃プラスチックを分解することが
可能となる作用を生じ、利用価値の高い燃料油を得られ
る作用を生じる。In the method for converting waste plastics into fuel oil according to the present invention having the above-mentioned structure, the waste plastics are discharged at a temperature of about 400 ° C. which is lower than the decomposition reaction temperature of 400 ° C. to 500 ° C. when a conventional catalyst is used. An effect is obtained that enables the plastic to be decomposed, and an effect that a fuel oil having high utility value can be obtained.
【0011】[0011]
【発明の実施の形態】(粘土鉱物)先ず、天然の粘土鉱
物について以下のように概観する。DETAILED DESCRIPTION OF THE INVENTION (Clay Mineral) First, a natural clay mineral will be outlined as follows.
【0012】天然に存在する粘土鉱物の組成はシリカ
(SiO2 )、アルミナ(Al2 O3)及び水を主成分
として、酸化鉄、酸化マグネシウム、酸化カルシウム、
ナトリウム及びカリウムなどの酸化物を含んでいる。最
も多く含む成分はシリカであり、シリカはSi4+に4個
のO2-が囲まれたSiO4 の四面体(Siを中心とした
各頂点に酸素イオンを配位している)を形成し、このS
i−O結合からなる四面体が2次元的に連続して、網状
につながって一つの四面体シートを作っている。そのほ
かに、この四面体シートと組み合うAl−O結合からな
る八面体(Alを中心に八面体の各頂点に酸素イオンを
配位している)の網状のつながりがある。すなわち、八
面体シートである。The composition of a naturally occurring clay mineral is mainly composed of silica (SiO 2 ), alumina (Al 2 O 3 ) and water, iron oxide, magnesium oxide, calcium oxide,
Contains oxides such as sodium and potassium. The component containing the most is silica, and silica forms a tetrahedron of SiO 4 in which four O 2− are surrounded by Si 4+ (oxygen ions are coordinated at each vertex centered on Si). And this S
A tetrahedral sheet composed of i-O bonds is two-dimensionally continuous and connected in a net-like fashion to form one tetrahedral sheet. In addition, there is a network connection of octahedrons composed of Al—O bonds combined with this tetrahedral sheet (oxygen ions are coordinated at each vertex of the octahedron with Al as the center). That is, it is an octahedral sheet.
【0013】粘土鉱物は両シートが1:1の割合で組合
わさった1:1層粘土と、2:1の割合で組合わさった
2:1層粘土に大きく分類できる。1:1層粘土として
はカオリナイト、ハロイサイト、蛇紋石などが知られて
いる。2:1層粘土としては雲母をはじめとしてモンモ
リロナイト、白土(モンモリロナイト−バイデライト系
のスメクタイトを主体とする微粒の粘土)、サポナイ
ト、セピオライト、パリゴルスカイトなど種類が多い。
又、上記の粘土鉱物が何種類か混合したものが天然には
存在している。尚、より詳細を表に纏めて下記する。Clay minerals can be broadly classified into 1: 1 clay in which both sheets are combined in a ratio of 1: 1 and 2: 1 clay in which both sheets are combined in a ratio of 2: 1. Kaolinite, halloysite, serpentine and the like are known as 1: 1 clay. There are many types of 2: 1 clay such as mica, montmorillonite, terra alba (montmorillonite-beiderite type fine clay mainly composed of smectite), saponite, sepiolite, and palygorskite.
A mixture of several kinds of the above clay minerals exists in nature. The details are summarized in the table below.
【0014】(粘土鉱物の分類) 1:1層粘土 カオリナイト、デイッカイト、ナクラ
イト、ハロイサイト、クリソタイル、アンチゴライト、
ペコライト、グリーナライト、カピオピライト、Alリ
ザーダイト 2:1層粘土 パイロフィライト、ミネソタアイト、
ケロライト、アライト、セリサイト、海緑石、緑泥石、
ドンバサイト、バーミキュライト、モンモリロナイト、
ハイデライト、ノントロナイト、サポナイト、ヘクトラ
イト、セピオライト、パリゴルスカイト その他、混合層鉱物として1:1層粘土と2:1層粘土
が混合したものがある。更に、非晶質ないし低結晶質鉱
物としてアロフェン、イモゴライトがある。(Classification of Clay Minerals) 1: 1 clay clay kaolinite, deckite, nacrite, halloysite, chrysotile, antigolite,
Pecolite, Greenerite, Capiopyrite, Al lizardite 2: 1 clay clay Pyrophyllite, Minnesotaite,
Kerolite, alite, sericite, chlorite, chlorite,
Donbasite, vermiculite, montmorillonite,
Hyderite, nontronite, saponite, hectorite, sepiolite, palygorskite, and other mixed layer minerals include a mixture of 1: 1 clay and 2: 1 clay. Further, there are allophane and imogolite as amorphous or low crystalline minerals.
【0015】粘土鉱物においては、前記したように1:
1層あるいは2:1層が主構成層になって、層状物質を
形成している。四面体あるいは八面体の中心元素がF
e、Mgイオンで置き変わっている場合は層自体が負の
電荷を持つことになる。そのため電荷を補うため層間に
はNa、K、Caの陽イオンが入り、交換可能なイオン
となっている。従って、それらの陽イオンを他の陽イオ
ンとイオン交換した新規の粘土鉱物を合成することがで
きる。あるいは層間に他の化合物を挿入(インターカレ
ーションという)したものも合成できる。In the clay mineral, as described above:
One layer or 2: 1 layer is a main constituent layer to form a layered material. The central element of the tetrahedron or octahedron is F
When the layer is replaced by e and Mg ions, the layer itself has a negative charge. Therefore, cations of Na, K, and Ca enter between the layers in order to supplement the charge, and become exchangeable ions. Therefore, a novel clay mineral in which those cations are ion-exchanged with other cations can be synthesized. Alternatively, a compound in which another compound is inserted between layers (referred to as intercalation) can also be synthesized.
【0016】(触媒の調製)次にこの発明の実施のため
の触媒の調製方法について説明する。 前記の粘土鉱物の項で説明したように天然の粘土鉱物
は層間にアルカリ及びアルカリ土類金属を復合させてい
る場合が多い。そこで、これらのイオンを単独のイオン
に統合させるために水溶性アルカリ及びアルカリ土類金
属の水溶液に粘土鉱物を入れ、半日ほど室温で攪拌させ
てイオン交換させる。交換後、陰イオンがなくなるまで
よく水洗し100℃で乾燥させる。このようにして層間
にアルカリ金属だけ、あるいはアルカリ土類金属だけを
挿入した粘土を調製することができる。 例えば、層間のイオンをプロトン(H+ )で置換した
粘土鉱物は、以下のようにして調製する。(Preparation of Catalyst) Next, a method of preparing a catalyst for carrying out the present invention will be described. As explained in the section on clay minerals, natural clay minerals often have alkali and alkaline earth metals incorporated between layers. Therefore, in order to integrate these ions into single ions, a clay mineral is added to an aqueous solution of a water-soluble alkali and an alkaline earth metal, and the mixture is stirred at room temperature for about half a day for ion exchange. After the exchange, wash well with water until the anions disappear, and dry at 100 ° C. In this way, a clay in which only an alkali metal or only an alkaline earth metal is inserted between layers can be prepared. For example, a clay mineral in which ions between layers are replaced with protons (H + ) is prepared as follows.
【0017】粘土鉱物を5〜20%(体積%、以下同
じ。)硫酸水溶液、あるいは塩酸水溶液、あるいは5〜
10%硝酸水溶液、あるいは10〜20%酢酸水溶液、
あるいはリン酸水溶液中に入れ、1〜2時間室温で攪拌
する。このように処理した粘土鉱物を水洗し、100℃
で乾燥して触媒とする。 上記で調製した層間にプロトンを挿入したものをア
ルミニウム及びランタンをはじめとする希土類元素の塩
の水溶液(1〜2mol/l)中に入れ、数時間室温で攪拌し
て、イオンで交換したものを作る。交換後よく水洗し1
00℃で乾燥させ触媒とする。 ニッケル、銅、亜鉛、クロム等を添加した粘土鉱物
は、以下のようにして調製する。The clay mineral is made up of 5 to 20% (vol%, hereinafter the same) aqueous sulfuric acid or aqueous hydrochloric acid, or
10% nitric acid aqueous solution, or 10-20% acetic acid aqueous solution,
Alternatively, it is placed in an aqueous phosphoric acid solution and stirred at room temperature for 1 to 2 hours. The clay mineral thus treated is washed with water,
And dried to obtain a catalyst. The solution prepared by inserting protons between the layers prepared above was placed in an aqueous solution of a salt of a rare earth element such as aluminum and lanthanum (1-2 mol / l), stirred at room temperature for several hours, and exchanged with ions. create. Wash thoroughly with water after replacement 1
It is dried at 00 ° C. to obtain a catalyst. A clay mineral to which nickel, copper, zinc, chromium, etc. are added is prepared as follows.
【0018】ニッケル、銅、亜鉛等の硝酸塩及び塩化物
又は三酸化クロムの水溶液に上記で処理した粘土鉱物
を入れ、攪拌後1日間室温で放置してから、濾過、水洗
し100℃で乾燥させる。のち500℃で数時間空気流
通下で焼成する。このまま触媒にして使用するか、水素
雰囲気中での反応の場合はあらかじめ反応前に水素流通
下、500℃で数時間還元する。ニッケル、銅、亜鉛、
クロムの添加量はそれぞれ金属として2〜20重量%で
ある。 チタニア、銅、ジルコニア、バナジウム酸化物等をイ
ンターカレートした粘土鉱物は、以下のようにして調製
する。The clay mineral treated as above is placed in an aqueous solution of nitrate such as nickel, copper, zinc or the like, chloride or chromium trioxide, left to stand at room temperature for 1 day after stirring, filtered, washed with water and dried at 100 ° C. . Then, it is calcined at 500 ° C. for several hours under air flow. It is used as a catalyst as it is, or in the case of a reaction in a hydrogen atmosphere, is reduced in advance at 500 ° C. for several hours under a hydrogen flow before the reaction. Nickel, copper, zinc,
The addition amount of chromium is 2 to 20% by weight as a metal. A clay mineral obtained by intercalating titania, copper, zirconia, vanadium oxide and the like is prepared as follows.
【0019】チタンテトライソプロポキシド又は銅エト
キシド又はジルコニウムオキシクロライド又はメチルオ
ルソバナジウム80重量%の酢酸水溶液と粘土と水から
なる懸濁液とを混合し、室温で攪拌後、1日放置して粘
土の層間に上記化合物を挿入させた。水洗後100℃で
乾燥させ、300℃空気中で2〜3時間焼成して触媒と
する。An aqueous acetic acid solution containing 80% by weight of titanium tetraisopropoxide or copper ethoxide or zirconium oxychloride or methyl orthovanadium is mixed with a suspension consisting of clay and water. The above compound was inserted between the layers. After washing with water, it is dried at 100 ° C. and calcined in air at 300 ° C. for 2 to 3 hours to obtain a catalyst.
【0020】[0020]
【実施例】以下、この発明の廃プラスチックの燃料油化
方法の実施例を実験結果を基に説明する。EXAMPLES Examples of the method for converting waste plastics into fuel oil according to the present invention will be described below based on experimental results.
【0021】図1及び図2は実験に使用した反応装置を
示す図であり、共に主としてガラス管からなる。図1に
示す反応装置1は廃プラスチックを分解する反応管R
と、生成物を捕集する液体窒素・トルエン冷媒のトラッ
プT2からなり、更に生成ガスを測定する流量計F2及
びガス生成物を捕集するテドラーバックTBからなって
いる。尚、図中符号Cはプラスチック及び触媒、Eは反
応管Rを加熱するための電気炉、TCは温度を測定する
ための熱電対、F1は供給するガスを測定するための流
量計である。FIG. 1 and FIG. 2 are views showing a reaction apparatus used in the experiment, and both are mainly composed of glass tubes. The reaction apparatus 1 shown in FIG.
And a trap T2 of liquid nitrogen / toluene refrigerant for collecting products, a flow meter F2 for measuring generated gas, and a Tedlar bag TB for collecting gas products. In the figure, reference symbol C denotes a plastic and a catalyst, E denotes an electric furnace for heating the reaction tube R, TC denotes a thermocouple for measuring temperature, and F1 denotes a flow meter for measuring gas to be supplied.
【0022】図2に示す反応装置2においては廃プラス
チックを分解する反応管Aの他にこれと連結して水素化
のための反応管Bが配され、生成物を捕集するトラップ
も氷水冷却トラップT1と液体窒素・トルエン冷媒のト
ラップT2が配される。尚、図中符号C1はプラスチッ
ク分解触媒、C2は水素化触媒又は骨格異性化触媒、F
2は生成ガスを測定する流量計、TBはガス生成物を捕
集するテドラーバック、E1は反応管Aを加熱するため
の電気炉、E2は反応管Bを加熱するための電気炉、T
Cは温度を測定するための熱電対、F1は供給するガス
を測定するための流量計、Kは供給するガスのコックで
ある。又、図中符号SはモータMにより駆動されるプラ
スチック供給器、Pはプラスチック導入口である。In the reactor 2 shown in FIG. 2, a reaction tube B for hydrogenation is connected in addition to a reaction tube A for decomposing waste plastic, and a trap for collecting products is also cooled with ice water. A trap T1 and a trap T2 for liquid nitrogen / toluene refrigerant are provided. In the figure, C1 is a plastic decomposition catalyst, C2 is a hydrogenation catalyst or a skeletal isomerization catalyst, F
2 is a flow meter for measuring product gas, TB is a Tedlar bag for collecting gas products, E1 is an electric furnace for heating the reaction tube A, E2 is an electric furnace for heating the reaction tube B, T
C is a thermocouple for measuring temperature, F1 is a flow meter for measuring gas to be supplied, and K is a cock for supplying gas. In the figure, reference symbol S denotes a plastic feeder driven by a motor M, and P denotes a plastic inlet.
【0023】水素を導入して水素雰囲気で反応を行う場
合、図1に示す反応装置1においてはプラスチック分解
触媒と水素化触媒とを混合し、あらかじめ所定の温度で
水素で触媒を還元してからプラスチック分解を行った。
又、水素化を別の反応器を用いて行う場合は図2に示す
反応装置2を用い、反応管Aにはプラスチック分解触媒
C1を、反応管Bには水素化触媒C2をそれぞれ入れ、
プラスチック分解と水素化反応とを異なる温度で行っ
た。すなわち、反応管Aに窒素ガスだけを所定の温度
(400〜500℃)で流し、反応管Bには水素だけを
所定の温度(400〜500℃)で3〜5時間流し還元
させた。還元後、水素を流しながら反応管Bを150〜
250℃の温度まで下げ、反応管Aと反応管Bとを接続
してからプラスチック供給器S(金属製)により廃プラ
スチックをゆっくり供給して反応させた。水素化反応を
行う場合は何れも水素と窒素の混合ガスを用いて行っ
た。When a reaction is carried out in a hydrogen atmosphere by introducing hydrogen, in a reaction apparatus 1 shown in FIG. 1, a plastic cracking catalyst and a hydrogenation catalyst are mixed, and the catalyst is reduced with hydrogen at a predetermined temperature in advance, and then, Plastic disassembly was performed.
When hydrogenation is carried out using another reactor, a reactor 2 shown in FIG. 2 is used, a plastic cracking catalyst C1 is placed in a reaction tube A, and a hydrogenation catalyst C2 is placed in a reaction tube B, respectively.
Plastic decomposition and hydrogenation reactions were performed at different temperatures. That is, only nitrogen gas was allowed to flow through the reaction tube A at a predetermined temperature (400 to 500 ° C.), and only hydrogen was allowed to flow through the reaction tube B at a predetermined temperature (400 to 500 ° C.) for 3 to 5 hours for reduction. After the reduction, while flowing hydrogen, the reaction tube B
The temperature was lowered to 250 ° C., the reaction tube A and the reaction tube B were connected, and waste plastic was slowly supplied by a plastic feeder S (made of metal) to cause a reaction. In each case of performing the hydrogenation reaction, a mixed gas of hydrogen and nitrogen was used.
【0024】何れの反応でも、反応管からプラスチック
分解にともなう白色の煙が出なくなった後0.5時間そ
のまま保持してから、反応を終了させた。液体及び気体
生成物の分析はガスクロマトグラフによった。液体及び
気体生成物の重量はトラップに捕集した液体及びテドラ
ーバックに捕集した気体生成物の重量を測定して求め
た。気体生成物の重量を測定する場合はガスクロマトグ
ラフによる分析結果を補正して求めた。又、反応管に残
留した物の重量は反応管の重量を直接測定し、反応前の
反応管の重量を差し引いて求めた。In each of the reactions, the reaction tube was maintained for 0.5 hour after the white smoke accompanying the decomposition of the plastic did not come out of the reaction tube, and then the reaction was terminated. Analysis of liquid and gaseous products was by gas chromatography. The weight of the liquid and gaseous products was determined by measuring the weight of the liquid collected in the trap and of the gaseous products collected in the Tedlar bag. When the weight of the gaseous product was measured, it was obtained by correcting the result of analysis by gas chromatography. The weight of the residue in the reaction tube was determined by directly measuring the weight of the reaction tube and subtracting the weight of the reaction tube before the reaction.
【0025】又、オレフィン、パラフィン、芳香族化合
物の分離定量分析は JIS K2536(1973)及びK2835 (19
73)記載の方法によって行った。The separation and quantitative analysis of olefins, paraffins, and aromatic compounds is described in JIS K2536 (1973) and K2835 (19
73) Performed by the method described.
【0026】(比較例)触媒を使用する分解反応を行う
前に無触媒でポリエチレン(以下PEと略す)を400
℃及び450℃で分解させたところ、PEの場合ワック
ス状のものだけが得られ、液状の油は得られなかった。
同様な反応挙動はポリプロピレン(以下PPと略す)の
400℃での分解の場合に見られた。これに対し、適当
な触媒を使用することによって以下に示すように400
℃及び450℃の比較的低温での分解反応で液状の分解
油が得られる。(Comparative Example) Polyethylene (hereinafter abbreviated as PE) was added without a catalyst to 400 before a decomposition reaction using a catalyst was carried out.
When it was decomposed at 400 ° C. and 450 ° C., in the case of PE, only a waxy product was obtained, and no liquid oil was obtained.
Similar reaction behavior was observed in the case of decomposition of polypropylene (hereinafter abbreviated as PP) at 400 ° C. On the other hand, by using an appropriate catalyst, 400
Liquid cracked oil is obtained by a cracking reaction at a relatively low temperature of 450C or 450C.
【0027】(実施例1)図1に示す反応装置1で、反
応管Rのみを使用し、以下の反応条件で廃プラスチック
の分解を行った。Example 1 In the reactor 1 shown in FIG. 1, only the reaction tube R was used, and the waste plastic was decomposed under the following reaction conditions.
【0028】 反応条件: 触媒量 1g PE(硬質)及びPP 20g 反応温度 400℃〜500℃ 窒素流速 60ml/min (標準状態) 窒素は予熱して350℃以上に熱せられて反応管に入っ
ている。従って、窒素流速は2.3〜2.8倍になって
反応管に入る。PE及びPPは供給器から0.5〜0.
7g/minの速度で連続的に供給した。又、水素と窒素の
混合ガスを供給するときは水素対窒素の混合割合を1〜
2:1〜5にして、全流速60〜100ml/minとした。Reaction conditions: Catalyst amount 1 g PE (hard) and PP 20 g Reaction temperature 400 ° C. to 500 ° C. Nitrogen flow rate 60 ml / min (standard condition) Nitrogen is preheated and heated to 350 ° C. or more and put in a reaction tube. . Therefore, the nitrogen flow rate is 2.3 to 2.8 times and enters the reaction tube. PE and PP are supplied from the feeder at 0.5-0.
It was fed continuously at a rate of 7 g / min. When supplying a mixed gas of hydrogen and nitrogen, the mixing ratio of hydrogen to nitrogen is 1 to
2: 1 to 5 for a total flow rate of 60 to 100 ml / min.
【0029】モンモリロナイト(天然の2:1層粘土)
を触媒とし、400℃でPEを分解した。気体状生成物
を取り出すために窒素ガスを流した。液体生成物は、供
給した原料に対し53%、気体生成物は5%、残りは残
査油(主としてワックス)及び炭素であった。液体生成
物は、炭素数4〜16ないし17までの炭化水素で、パ
ラフィンとオレフィンが64対36からなるものであっ
た。芳香族化合物はほとんど含まれてない。気体生成物
は、炭素数1〜4までの炭化水素でパラフィンとオレフ
ィンからなっていた。パラフィンとオレフィン比は液体
生成物の場合とほぼ一致した。又水素の生成も認めら
れ、その量は全ガス量の2体積%であった。Montmorillonite (natural 2: 1 clay)
Was used as a catalyst to decompose PE at 400 ° C. Nitrogen gas was flowed to remove gaseous products. The liquid product was 53% of the feed fed, the gaseous product 5% and the balance was residual oil (mainly wax) and carbon. The liquid product was a hydrocarbon of from 4 to 16 to 17 carbon atoms, consisting of paraffins and olefins of 64:36. Almost no aromatic compounds are contained. The gaseous product was a hydrocarbon having from 1 to 4 carbon atoms and consisted of paraffins and olefins. The paraffin to olefin ratio was almost identical to that of the liquid product. The generation of hydrogen was also recognized, and the amount was 2% by volume of the total gas amount.
【0030】(実施例2)実施例1と同一の反応装置・
反応条件で、パリゴルスカイト(天然の2:1層粘土)
を触媒としてPEの分解を450℃で行った。液体生成
物68%、気体生成物は6%、残りは残査油及び炭素で
あった。液体生成物のうち炭素数5の炭化水素、C5 は
13%、以下C6 7%、C7 4%、C8 8%、C9 34
%、C10〜33%、気体生成物のうち水素2%、C1 4
1%、C2 30%、C3 16%、C 4 11%となった。(Example 2) The same reaction apparatus as in Example 1
Under reaction conditions, palygorskite (natural 2: 1 layer clay)
Was used as a catalyst to decompose PE at 450 ° C. Liquid generation
68% gaseous products, 6% gaseous products, the balance being residual oil and carbon
there were. C5 hydrocarbons in the liquid product, CFiveIs
13%, below C67%, C74%, C88%, C934
%, CTen~ 33%, hydrogen 2% of gaseous product, C14
1%, CTwo30%, CThree16%, C FourIt was 11%.
【0031】(実施例3)実施例1と同一の反応装置・
反応条件で、酸処理したモンモリロナイトを触媒とし、
400℃でPEを分解した。液体生成物68%、気体生
成物は7%、残りは残査油及び炭素であった。液体生成
物のうちC5 13%、C6 7%、C7 8%、C8 8%、
C9 30%、C10〜33%、気体生成物のうち水素3
%、C1 38%、C2 29%、C3 19%、C4 11%
となった。(Example 3) The same reactor as in Example 1
Under the reaction conditions, using montmorillonite treated with acid as a catalyst,
The PE was decomposed at 400 ° C. 68% liquid product, 7% gaseous product, balance oil and carbon. 13% of C 5 , 7% of C 6 , 8% of C 7, 8% of C 8 ,
C 9 30%, C 10 -33%, hydrogen 3 among gaseous products
%, C 1 38%, C 2 29%, C 3 19%, C 4 11%
It became.
【0032】(実施例4)実施例1と同一の反応装置・
反応条件で、酸処理したパリゴルスカイトを触媒に用い
てPEの分解を450℃で行った。液体生成物は81
%、気体生成物は10%、残りは残査油及び炭素であっ
た。(Example 4) The same reactor as in Example 1
Under the reaction conditions, PE was decomposed at 450 ° C. using an acid-treated palygorskite as a catalyst. 81 liquid products
%, 10% gaseous products, the balance being residual oil and carbon.
【0033】(実施例5)実施例1と同一の反応装置・
反応条件で、酸処理したセピオライト(天然の2:1層
粘土)を触媒としてPPの分解を450℃で行った。液
体生成物は85%、気体生成物は8%、残りは残査油及
び炭素であった。(Example 5) The same reaction apparatus as in Example 1
Under the reaction conditions, PP was decomposed at 450 ° C. using acid-treated sepiolite (natural 2: 1 layer clay) as a catalyst. The liquid product was 85%, the gaseous product was 8%, the balance was residual oil and carbon.
【0034】(実施例6)実施例1と同一の反応装置・
反応条件で、パリゴルスカイトに酸化亜鉛を添加した触
媒を用いてPEの分解を450℃で行った。液体生成物
は87%、気体生成物は11%、残りは残査油及び炭素
で、残査油及び炭素の生成量が少なくなった。パラフィ
ン対オレフィン体積比は74:26で、パラフィンに富
んだ油が得られた。(Example 6) The same reactor as in Example 1
Under the reaction conditions, PE was decomposed at 450 ° C. using a catalyst in which zinc oxide was added to palygorskite. The liquid product was 87%, the gaseous product was 11%, and the remainder was residual oil and carbon, producing less residual oil and carbon. A paraffin to olefin volume ratio of 74:26 yielded a paraffin-rich oil.
【0035】(実施例7)実施例1と同一の反応装置・
反応条件で、パリゴルスカイト中のカチオンをランタン
イオンで交換した触媒を用いてPPを400℃で分解し
た。液体生成物は65%、気体生成物は5%、残りは残
査油及び炭素であった。(Example 7) The same reactor as in Example 1
Under the reaction conditions, PP was decomposed at 400 ° C. using a catalyst in which cations in palygorskite were exchanged with lanthanum ions. The liquid product was 65%, the gaseous product was 5%, the balance was residual oil and carbon.
【0036】(実施例8)実施例1と同一の反応装置・
反応条件で、パリゴルスカイトに酸化クロムを添加した
触媒を用いてPEの分解を500℃で行った。液体生成
物は87%、気体生成物は10%、残りは残査油及び炭
素であった。Example 8 The same reaction apparatus as in Example 1
Under the reaction conditions, PE was decomposed at 500 ° C. using a catalyst obtained by adding chromium oxide to palygorskite. The liquid product was 87%, the gaseous product was 10%, the balance was residual oil and carbon.
【0037】(実施例9)実施例1と同一の反応装置・
反応条件で、パリゴルスカイトに銅(酸化物)を添加し
た触媒を用いてPEの分解を450℃で行った。液体生
成物は90%、気体生成物は8%、残りは残査油及び炭
素であった。(Example 9) The same reactor as in Example 1
Under the reaction conditions, PE was decomposed at 450 ° C. using a catalyst in which copper (oxide) was added to palygorskite. The liquid product was 90%, the gaseous product was 8%, the balance was residual oil and carbon.
【0038】以上の実施例において、酸処理した粘土鉱
物及びそれらに金属酸化物(酸化亜鉛、酸化クロム、酸
化銅等)を添加した触媒を使用した方が、何も処理して
いない同一の粘土鉱物触媒に比べて液体、気体の生成物
量がいずれも多かった。すなわち、廃プラスチックの分
解には酸処理及び金属酸化物を添加した粘土鉱物の方が
触媒としてより有効であることがわかる。尚、強酸又は
弱酸どちらの酸で処理しても触媒としての機能には変わ
りはなかった。In the above embodiments, the use of an acid-treated clay mineral and a catalyst obtained by adding a metal oxide (zinc oxide, chromium oxide, copper oxide, etc.) to the clay mineral were the same. Both liquid and gaseous product amounts were higher than the mineral catalyst. That is, it is understood that the clay mineral to which the acid treatment and the metal oxide are added is more effective as a catalyst for decomposing the waste plastic. In addition, the function as a catalyst did not change even when treated with either a strong acid or a weak acid.
【0039】(実施例10)図2に示す反応装置2で、
反応管A及び反応管Bを使用し、以下の反応条件で廃プ
ラスチック分解を行った。Example 10 In the reactor 2 shown in FIG.
Using the reaction tube A and the reaction tube B, waste plastic was decomposed under the following reaction conditions.
【0040】 反応条件: 触媒量 反応管A 1g 反応管B 0.5g 反応温度 反応管A 400〜450℃ 反応管B 200〜300℃ 窒素流速 30〜60ml/min (標準状態) 水素流速 30〜45ml/min (標準状態) PE(硬質)及びPP 20g 酸処理したパリゴルスカイトならびに酸化亜鉛を添加し
たものを触媒として入れ、450℃でPEの分解を行っ
た。キャリアーガスとして窒素のみを供給した。液体生
成物は88%、気体生成物は7%、残査油及び炭素は5
%となった。パラフィン対オレフィンの比は76:24
になった。Reaction conditions: amount of catalyst 1 g of reaction tube A 0.5 g of reaction tube B Reaction temperature Reaction tube A 400 to 450 ° C. Reaction tube B 200 to 300 ° C. Nitrogen flow rate 30 to 60 ml / min (standard condition) Hydrogen flow rate 30 to 45 ml / min (standard state) PE (hard) and 20 g of PP A mixture of acid-treated palygorskite and zinc oxide was added as a catalyst, and PE was decomposed at 450 ° C. Only nitrogen was supplied as a carrier gas. 88% liquid product, 7% gaseous product, 5% residual oil and carbon
%. The paraffin to olefin ratio is 76:24
Became.
【0041】(実施例11)実施例10の反応系に水素
を加えて同一の反応条件下で反応させた。なお混合触媒
は前もって450℃で3時間水素還元を行った。液体生
成物は88%、気体生成物は9%、残査油及び炭素は3
%となった。気体生成物中には未反応の水素が含まれて
いるので、気体生成物量の値は多少少なくなると思われ
る。残査油中にはワックス状のものは見られず、炭素の
みと考えられるが、その量も水素共存下では少なくなっ
ている。パラフィン対オレフィンの比は98:2にな
り、パラフィンの割合が増大した。Example 11 Hydrogen was added to the reaction system of Example 10 and reacted under the same reaction conditions. The mixed catalyst was previously subjected to hydrogen reduction at 450 ° C. for 3 hours. 88% liquid product, 9% gaseous product, 3% residual oil and carbon
%. Since the unreacted hydrogen is contained in the gaseous product, the value of the gaseous product amount is expected to be slightly smaller. No waxy substance was found in the residual oil, and it is considered that only carbon was present, but the amount thereof was reduced in the presence of hydrogen. The paraffin to olefin ratio was 98: 2 and the paraffin ratio was increased.
【0042】(実施例12)実施例10と同一の反応装
置・反応条件で、酸処理したパリゴルスカイトならびに
酸化ニッケル・シリカ触媒を混合したものを反応管に入
れ、450℃でPPの分解を行った。触媒は前もって4
50℃で3時間水素還元を行った。液体生成物は83
%、気体生成物は15%、残査油及び炭素は2%となっ
た。生成物はほぼ100%パラフィンから成っていた。
C6 からC11程度の生成油性分にはガソリン成分(枝分
かれしたパラフィン系炭化水素)が多く生成した。Example 12 A mixture of an acid-treated palygorskite and a nickel oxide / silica catalyst was placed in a reaction tube under the same reactor and reaction conditions as in Example 10, and PP was decomposed at 450 ° C. . Catalyst 4 in advance
Hydrogen reduction was performed at 50 ° C. for 3 hours. 83 liquid products
%, Gaseous products 15%, residual oil and carbon 2%. The product consisted of almost 100% paraffin.
The product oil fraction of about C 11 from C 6 to produce many gasoline component (branched paraffinic hydrocarbons).
【0043】このような方法によるPE及びPPの分解
は水素化触媒による分解が促進されるためか、液体生成
物の量が少なくなり、それに反して気体生成物量が増大
した。分子量の小さいガス状の生成物を多く作る目的な
らばこの方法は適している。The decomposition of PE and PP by such a method may be due to the accelerated decomposition by the hydrogenation catalyst, possibly resulting in a decrease in the amount of the liquid product and an increase in the amount of the gas product. This method is suitable for producing many gaseous products having a low molecular weight.
【0044】(実施例13)実施例10と同一の反応装
置・反応条件で、反応管Aには酸処理したパリゴルスカ
イトを、反応管Bにはパリゴルスカイトに酸化亜鉛を添
加した触媒を充填し、あらかじめ水素を450℃、3〜
5時間流し還元した。反応管Aには窒素ガスを、反応管
Bには水素を流しPEの分解を450℃で行った。反応
管Bの温度は300℃に保った。液体生成物は88%、
気体生成物は11%、残査油及び炭素は1%となった。(Example 13) Under the same reaction apparatus and reaction conditions as in Example 10, a reaction tube A was filled with an acid-treated palygorskite, and a reaction tube B was filled with a catalyst obtained by adding zinc oxide to palygorskite. Hydrogen at 450 ° C, 3 ~
The solution was reduced by flowing for 5 hours. Nitrogen gas was supplied to the reaction tube A, and hydrogen was supplied to the reaction tube B to decompose PE at 450 ° C. The temperature of the reaction tube B was kept at 300 ° C. 88% liquid product,
The gaseous product was 11% and the residual oil and carbon were 1%.
【0045】(実施例14)実施例10と同一の反応装
置・反応条件で、反応管Aには酸処理したパリゴルスカ
イトを、反応管Bにはパリゴルスカイトに酸化ニッケル
を添加した触媒を充填し、あらかじめ水素を450℃、
3〜5時間流し還元した。反応管Aには窒素ガスを、反
応管Bには水素を流しPEの分解を450℃で行った。
反応管Bの温度は300℃に保った。液体生成物は91
%、気体生成物は8%、残査油及び炭素は1%となっ
た。液体生成物中の成分組成はC5 9%、C6 11%、
C7 11%、C8 9%、C9 8%、C108%、C11〜4
4%となった。又、気体生成物のうちC1 29%、C2
63%、C3 4%、C4 4%となった。(Example 14) Under the same reactor and reaction conditions as in Example 10, the reaction tube A was filled with an acid-treated palygorskite, and the reaction tube B was filled with a catalyst obtained by adding nickel oxide to palygorskite. 450 ° C hydrogen
The solution was reduced by flowing for 3 to 5 hours. Nitrogen gas was supplied to the reaction tube A, and hydrogen was supplied to the reaction tube B to decompose PE at 450 ° C.
The temperature of the reaction tube B was kept at 300 ° C. The liquid product is 91
%, Gaseous products 8%, residual oil and carbon 1%. Composition of liquid product C 5 9%, C 6 11 %,
C 7 11%, C 8 9 %, C 9 8%, C 10 8%, C 11 ~4
It was 4%. Also, 29% of C 1 , C 2
63%, C 3 4% and C 4 4%.
【0046】(実施例15)実施例10と同一の反応装
置・反応条件で、反応管Aには酸処理したセピオライト
を、反応管Bにはシリカ担持酸化ニッケル・カルシア触
媒を充填し、あらかじめ水素を450℃、3〜5時間流
し還元した。反応管Aでの反応温度は500℃、反応管
Bでの反応温度は200℃で行った。液体生成物は90
%、気体生成物は10%、残査油及び炭素は0%となっ
た。液体生成物中のパラフィン対オレフィン比はほぼ1
対0になり、100%パラフィン系の燃料油となった。(Example 15) Under the same reaction apparatus and reaction conditions as in Example 10, acid-treated sepiolite was filled in reaction tube A, and nickel oxide-calcia catalyst supported on silica was filled in reaction tube B. At 450 ° C. for 3 to 5 hours for reduction. The reaction temperature in the reaction tube A was 500 ° C., and the reaction temperature in the reaction tube B was 200 ° C. The liquid product is 90
%, Gaseous products 10%, residual oil and carbon 0%. The paraffin to olefin ratio in the liquid product is approximately 1
It became 0, and became 100% paraffin-based fuel oil.
【0047】図1に示す反応装置1及び図2に示す反応
装置2を用いて、以上の方法によりポリエチレン及びポ
リプロピレンを接触分解させた場合、得られた油は主と
して軽油(直鎖の炭化水素)で、後者の場合はガソリン
留分(枝分かれのある炭化水素)も含まれている。ポリ
エチレンを接触分解して得られる油中にもガソリン留分
を、又、ポリプロピレン接触分解油中にもガソリン留分
をより多く含むようにすることが燃料としての付加価値
を上げると考える。When polyethylene and polypropylene are subjected to catalytic cracking by the above method using the reactor 1 shown in FIG. 1 and the reactor 2 shown in FIG. 2, the obtained oil is mainly light oil (linear hydrocarbon). In the latter case, a gasoline fraction (a branched hydrocarbon) is also included. Increasing the gasoline fraction in the oil obtained by catalytic cracking of polyethylene and the gasoline fraction in the catalytic cracking oil of polypropylene will increase the added value as a fuel.
【0048】(実施例16)図2に示す反応装置の反応
管Bに骨格異性化作用のある触媒を0.5〜1g入れ、
窒素、水素混合ガスを流しながら150〜250℃で反
応を行った。反応管Aには酸処理したパリゴルスカイト
触媒を入れ、400〜450℃でポリエチレンを分解し
た。得られた油中にはガソリン留分が30〜45%認め
られた。(Example 16) 0.5 to 1 g of a catalyst having a skeletal isomerization action was placed in a reaction tube B of the reactor shown in FIG.
The reaction was performed at 150 to 250 ° C. while flowing a mixed gas of nitrogen and hydrogen. An acid-treated palygorskite catalyst was placed in the reaction tube A, and polyethylene was decomposed at 400 to 450 ° C. A gasoline fraction of 30 to 45% was found in the obtained oil.
【0049】[0049]
【発明の効果】以上の構成よりなるこの発明の燃料油化
方法によれば、触媒に天然の粘土鉱物をそのまま使用す
る他、それらを酸で処理して酸性を持たせたもの、又は
粘土鉱物がもつ陽イオン交換性を利用して各種のイオン
で交換修飾したもの、又は粘土鉱物にニッケル、亜鉛、
銅、酸化クロム等の金属ならびに金属酸化物を添加した
もの、又は粘土鉱物の層状構造に基づく層間にジルコニ
ア、銅、チタニア、バナジア等を挿入したもの、又はこ
れらを組み合わせて活性を向上させたものを使用するこ
とにより、廃プラスチックの熱分解を従来の無触媒分解
に比べて短い時間で、しかも省エネルギーで行うことが
でき、しかも、利用価値の高い燃料油を得られることが
できる。According to the fuel oil conversion method of the present invention having the above-mentioned structure, a natural clay mineral is used as a catalyst as it is, and the clay mineral is treated with an acid to make it acidic or a clay mineral. Exchange-modified with various ions utilizing the cation exchange property of the clay mineral or nickel, zinc,
Copper, chromium oxide and other metals and metal oxides added, or zirconia, copper, titania, vanadia, etc. inserted between layers based on the layered structure of clay minerals, or those with improved activity by combining these By using, the thermal decomposition of waste plastic can be performed in a shorter time than conventional non-catalytic decomposition with less energy consumption, and a highly useful fuel oil can be obtained.
【0050】一方、粘土鉱物は従来公知の触媒に比し安
価なので、上記の省エネルギー効果と相まって低コスト
で燃料油化を行うことが可能となり、しかも、得られる
分解生成物も利用価値の高い燃料油なのでリサイクル性
が高く、熱分解して油化するという廃プラスチックの処
理手段の実用化への一指針となる有益な実用的発明であ
る。On the other hand, since clay minerals are inexpensive as compared with conventionally known catalysts, it becomes possible to convert fuel oil into fuel oil at low cost in combination with the above-mentioned energy saving effect. Since it is oil, it is highly recyclable, and is a useful practical invention that can be a guide to the practical use of waste plastic treatment means that is thermally decomposed into oil.
【図1】 この発明を実施するための反応装置の断面
図。FIG. 1 is a cross-sectional view of a reactor for carrying out the present invention.
【図2】 同上、異なる実施例の反応装置の断面図。FIG. 2 is a sectional view of a reaction apparatus according to another embodiment of the present invention;
1 反応装置 2 反応装置 1 reactor 2 reactor
───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4F301 AA13 AA14 AA15 AD02 BA21 BE35 BE44 BF20 BF31 BG50 4G069 AA01 AA08 AA15 BA10A BA10B BB02A BB04A BB10A BB10B BB12A BB12B BB14A BB14B BC31A BC31B BC35A BC35B BC38A BC42B BC58A BC58B BC68A BC68B CA10 CA11 DA06 EC22Y FA01 FB30 FB77 FB79 4H029 CA01 CA09 ──────────────────────────────────────────────────続 き Continuing on the front page F term (reference) 4F301 AA13 AA14 AA15 AD02 BA21 BE35 BE44 BF20 BF31 BG50 4G069 AA01 AA08 AA15 BA10A BA10B BB02A BB04A BB10A BB10B BB14B38BBC BCBC BC BC BC EC22Y FA01 FB30 FB77 FB79 4H029 CA01 CA09
Claims (9)
収するにあたり、1:1層粘土鉱物に分類される粘土鉱
物を触媒として用いることを特徴とする廃プラスチック
の燃料油化方法。1. A method for converting waste plastic to fuel oil, comprising using, as a catalyst, a clay mineral classified as a 1: 1 clay mineral when recovering fuel oil by pyrolyzing the waste plastic.
収するにあたり、2:1層粘土鉱物に分類される粘土鉱
物を触媒として用いることを特徴とする廃プラスチック
の燃料油化方法。2. A method for converting waste plastics to fuel oil, comprising using a clay mineral classified as a 2: 1 clay mineral as a catalyst in recovering the fuel oil by pyrolyzing the waste plastics.
触媒として用いる請求項1又は2記載の廃プラスチック
の燃料油化方法。3. The process for converting waste plastics into fuel oil according to claim 1, wherein a clay mineral treated with an acid to impart acidity is used as a catalyst.
弱酸として酢酸又はリン酸を用いた請求項3記載の廃プ
ラスチックの燃料油化方法。4. The method according to claim 3, wherein a strong acid such as sulfuric acid, nitric acid or hydrochloric acid is used as an acid and acetic acid or phosphoric acid is used as a weak acid.
の陽イオンとイオン交換したものを触媒として用いる請
求項1から4の何れかに記載の廃プラスチックの燃料油
化方法。5. The method according to claim 1, wherein a cation present between the layers of the clay mineral is exchanged with another cation for use as a catalyst.
である請求項5記載の廃プラスチックの燃料油化方法。6. The method according to claim 5, wherein the cation to be exchanged is an ion of a rare earth element.
酸化物を添加した粘土鉱物、又はこれと酸性を付与した
粘土鉱物を混合したものを触媒として用いる請求項3又
は4記載の廃プラスチックの燃料油化方法。7. The waste plastic according to claim 3, wherein a clay mineral obtained by adding a metal or a metal oxide to a clay mineral having acidity, or a mixture of a clay mineral having acidity and a clay mineral having acidity is used as a catalyst. Fuel oil conversion method.
化物は酸化クロムである請求項7記載の廃プラスチック
の燃料油化方法。8. The method according to claim 7, wherein the metal is nickel, copper or zinc, and the metal oxide is chromium oxide.
油化方法を水素雰囲気中で実施することにより、パラフ
ィン系炭化水素に富んだ油を回収する廃プラスチックの
燃料油化方法。9. A method for converting waste plastics into a fuel oil by recovering oil rich in paraffinic hydrocarbons by performing the fuel oil conversion method according to claim 3 or 4 or 7 or 8 in a hydrogen atmosphere.
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JP2534099A JP2000219884A (en) | 1999-02-02 | 1999-02-02 | Conversion of plastic waste to fuel oil |
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Cited By (4)
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---|---|---|---|---|
WO2016175706A1 (en) * | 2015-04-30 | 2016-11-03 | Nanyang Technological University | A pillared clay catalyst |
WO2021048185A1 (en) * | 2019-09-09 | 2021-03-18 | Basell Poliolefine Italia S.R.L. | Plastic depolymerization using halloysite |
WO2022090506A1 (en) * | 2020-10-30 | 2022-05-05 | Basell Poliolefine Italia S.R.L. | Supported metal oxides as depolymerization catalysts |
GR1010482B (en) * | 2022-01-24 | 2023-06-12 | Γεωργιος Παναγιωτη Παπαδεας | Fuel-producing method via plastic material treatment |
-
1999
- 1999-02-02 JP JP2534099A patent/JP2000219884A/en active Pending
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2016175706A1 (en) * | 2015-04-30 | 2016-11-03 | Nanyang Technological University | A pillared clay catalyst |
WO2021048185A1 (en) * | 2019-09-09 | 2021-03-18 | Basell Poliolefine Italia S.R.L. | Plastic depolymerization using halloysite |
CN114364727A (en) * | 2019-09-09 | 2022-04-15 | 巴塞尔聚烯烃意大利有限公司 | Depolymerization of plastics using halloysite |
US11319424B2 (en) | 2019-09-09 | 2022-05-03 | Basell Poliolefine Italia S.R.L. | Plastic depolymerization using halloysite |
KR20220062320A (en) * | 2019-09-09 | 2022-05-16 | 바셀 폴리올레핀 이탈리아 에스.알.엘 | Depolymerization of plastics using halloysite |
JP2022542193A (en) * | 2019-09-09 | 2022-09-29 | バーゼル・ポリオレフィン・イタリア・ソチエタ・ア・レスポンサビリタ・リミタータ | Plastic depolymerization using halloysite |
KR102650762B1 (en) * | 2019-09-09 | 2024-03-22 | 바셀 폴리올레핀 이탈리아 에스.알.엘 | Plastic depolymerization using halloysite |
WO2022090506A1 (en) * | 2020-10-30 | 2022-05-05 | Basell Poliolefine Italia S.R.L. | Supported metal oxides as depolymerization catalysts |
US11767408B2 (en) | 2020-10-30 | 2023-09-26 | Basell Poliolefine Italia S.R.L. | Supported metal oxides as depolymerization catalysts |
GR1010482B (en) * | 2022-01-24 | 2023-06-12 | Γεωργιος Παναγιωτη Παπαδεας | Fuel-producing method via plastic material treatment |
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