CA2085758A1 - Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brines - Google Patents
Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brinesInfo
- Publication number
- CA2085758A1 CA2085758A1 CA002085758A CA2085758A CA2085758A1 CA 2085758 A1 CA2085758 A1 CA 2085758A1 CA 002085758 A CA002085758 A CA 002085758A CA 2085758 A CA2085758 A CA 2085758A CA 2085758 A1 CA2085758 A1 CA 2085758A1
- Authority
- CA
- Canada
- Prior art keywords
- catalyst
- catalysts
- catalyst carrier
- washing
- gases
- 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.)
- Abandoned
Links
- 238000000034 method Methods 0.000 title claims abstract description 100
- 239000007789 gas Substances 0.000 title claims abstract description 45
- 239000000126 substance Substances 0.000 title claims abstract description 25
- 239000003054 catalyst Substances 0.000 claims abstract description 166
- 238000005406 washing Methods 0.000 claims abstract description 41
- 239000000758 substrate Substances 0.000 claims abstract description 31
- 239000000969 carrier Substances 0.000 claims abstract description 25
- 238000006243 chemical reaction Methods 0.000 claims abstract description 19
- 230000033558 biomineral tissue development Effects 0.000 claims abstract description 14
- 238000013032 photocatalytic reaction Methods 0.000 claims abstract description 4
- 239000007788 liquid Substances 0.000 claims description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 17
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 14
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 13
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical group O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 13
- 230000008569 process Effects 0.000 claims description 13
- 239000002245 particle Substances 0.000 claims description 11
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 11
- 229910052751 metal Inorganic materials 0.000 claims description 10
- 239000002184 metal Substances 0.000 claims description 10
- 230000000737 periodic effect Effects 0.000 claims description 9
- 229910001220 stainless steel Inorganic materials 0.000 claims description 9
- 239000010935 stainless steel Substances 0.000 claims description 9
- 239000000463 material Substances 0.000 claims description 8
- 239000007864 aqueous solution Substances 0.000 claims description 7
- 229910052729 chemical element Inorganic materials 0.000 claims description 7
- 229910052763 palladium Inorganic materials 0.000 claims description 7
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 7
- 238000005507 spraying Methods 0.000 claims description 7
- 229910021529 ammonia Inorganic materials 0.000 claims description 6
- 230000001590 oxidative effect Effects 0.000 claims description 6
- 229910052697 platinum Inorganic materials 0.000 claims description 6
- 239000010453 quartz Substances 0.000 claims description 6
- 239000004065 semiconductor Substances 0.000 claims description 6
- 239000004408 titanium dioxide Substances 0.000 claims description 6
- 238000003287 bathing Methods 0.000 claims description 5
- 150000003057 platinum Chemical class 0.000 claims description 5
- 229910052719 titanium Inorganic materials 0.000 claims description 5
- 239000010936 titanium Substances 0.000 claims description 5
- 229910052726 zirconium Inorganic materials 0.000 claims description 5
- 150000001255 actinides Chemical class 0.000 claims description 4
- 230000007797 corrosion Effects 0.000 claims description 4
- 238000005260 corrosion Methods 0.000 claims description 4
- 229910052735 hafnium Inorganic materials 0.000 claims description 4
- 150000002602 lanthanoids Chemical class 0.000 claims description 4
- 150000002739 metals Chemical class 0.000 claims description 4
- 229910052758 niobium Inorganic materials 0.000 claims description 4
- 239000010955 niobium Substances 0.000 claims description 4
- 230000001699 photocatalysis Effects 0.000 claims description 4
- 238000007788 roughening Methods 0.000 claims description 4
- 229910052715 tantalum Inorganic materials 0.000 claims description 4
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims description 3
- QCWXUUIWCKQGHC-UHFFFAOYSA-N Zirconium Chemical compound [Zr] QCWXUUIWCKQGHC-UHFFFAOYSA-N 0.000 claims description 3
- 229910052768 actinide Inorganic materials 0.000 claims description 3
- 229910052747 lanthanoid Inorganic materials 0.000 claims description 3
- 230000007774 longterm Effects 0.000 claims description 3
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- 239000002798 polar solvent Substances 0.000 claims description 3
- 239000011148 porous material Substances 0.000 claims description 3
- 239000010970 precious metal Substances 0.000 claims description 3
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims description 3
- 229910052727 yttrium Inorganic materials 0.000 claims description 3
- VWQVUPCCIRVNHF-UHFFFAOYSA-N yttrium atom Chemical compound [Y] VWQVUPCCIRVNHF-UHFFFAOYSA-N 0.000 claims description 3
- 229920000049 Carbon (fiber) Polymers 0.000 claims description 2
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 claims description 2
- 230000006399 behavior Effects 0.000 claims description 2
- 239000004917 carbon fiber Substances 0.000 claims description 2
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical group O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 2
- VBJZVLUMGGDVMO-UHFFFAOYSA-N hafnium atom Chemical compound [Hf] VBJZVLUMGGDVMO-UHFFFAOYSA-N 0.000 claims description 2
- GUCVJGMIXFAOAE-UHFFFAOYSA-N niobium atom Chemical compound [Nb] GUCVJGMIXFAOAE-UHFFFAOYSA-N 0.000 claims description 2
- 238000006068 polycondensation reaction Methods 0.000 claims description 2
- 229910052703 rhodium Inorganic materials 0.000 claims description 2
- 239000010948 rhodium Substances 0.000 claims description 2
- 229910052707 ruthenium Inorganic materials 0.000 claims description 2
- 229910052706 scandium Inorganic materials 0.000 claims description 2
- SIXSYDAISGFNSX-UHFFFAOYSA-N scandium atom Chemical compound [Sc] SIXSYDAISGFNSX-UHFFFAOYSA-N 0.000 claims description 2
- 230000001360 synchronised effect Effects 0.000 claims description 2
- GUVRBAGPIYLISA-UHFFFAOYSA-N tantalum atom Chemical compound [Ta] GUVRBAGPIYLISA-UHFFFAOYSA-N 0.000 claims description 2
- 229910052720 vanadium Inorganic materials 0.000 claims description 2
- 239000003575 carbonaceous material Substances 0.000 claims 1
- 229910010293 ceramic material Inorganic materials 0.000 claims 1
- 150000003841 chloride salts Chemical class 0.000 claims 1
- 229910000449 hafnium oxide Inorganic materials 0.000 claims 1
- WIHZLLGSGQNAGK-UHFFFAOYSA-N hafnium(4+);oxygen(2-) Chemical group [O-2].[O-2].[Hf+4] WIHZLLGSGQNAGK-UHFFFAOYSA-N 0.000 claims 1
- RVTZCBVAJQQJTK-UHFFFAOYSA-N oxygen(2-);zirconium(4+) Chemical compound [O-2].[O-2].[Zr+4] RVTZCBVAJQQJTK-UHFFFAOYSA-N 0.000 claims 1
- 238000007747 plating Methods 0.000 claims 1
- 238000009736 wetting Methods 0.000 claims 1
- 229910001928 zirconium oxide Inorganic materials 0.000 claims 1
- 230000003197 catalytic effect Effects 0.000 abstract description 14
- 239000003344 environmental pollutant Substances 0.000 description 21
- 231100000719 pollutant Toxicity 0.000 description 20
- 238000000746 purification Methods 0.000 description 20
- 239000003570 air Substances 0.000 description 13
- 239000000835 fiber Substances 0.000 description 12
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 10
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 9
- 239000000047 product Substances 0.000 description 9
- 239000000443 aerosol Substances 0.000 description 8
- 239000000243 solution Substances 0.000 description 8
- QGJOPFRUJISHPQ-UHFFFAOYSA-N Carbon disulfide Chemical compound S=C=S QGJOPFRUJISHPQ-UHFFFAOYSA-N 0.000 description 7
- 239000000203 mixture Substances 0.000 description 7
- 239000002351 wastewater Substances 0.000 description 7
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 6
- HEDRZPFGACZZDS-UHFFFAOYSA-N Chloroform Chemical compound ClC(Cl)Cl HEDRZPFGACZZDS-UHFFFAOYSA-N 0.000 description 6
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 6
- 229910018503 SF6 Inorganic materials 0.000 description 6
- 150000001875 compounds Chemical class 0.000 description 6
- 239000011521 glass Substances 0.000 description 6
- 238000004519 manufacturing process Methods 0.000 description 6
- SFZCNBIFKDRMGX-UHFFFAOYSA-N sulfur hexafluoride Chemical compound FS(F)(F)(F)(F)F SFZCNBIFKDRMGX-UHFFFAOYSA-N 0.000 description 6
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 5
- 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 5
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 5
- 150000002500 ions Chemical class 0.000 description 5
- 239000011734 sodium Substances 0.000 description 5
- 229910052708 sodium Inorganic materials 0.000 description 5
- 239000007921 spray Substances 0.000 description 5
- -1 H2S and scatoles Chemical class 0.000 description 4
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 4
- 239000011248 coating agent Substances 0.000 description 4
- 238000000576 coating method Methods 0.000 description 4
- 229910052736 halogen Inorganic materials 0.000 description 4
- 150000002367 halogens Chemical class 0.000 description 4
- 230000001965 increasing effect Effects 0.000 description 4
- 150000003839 salts Chemical class 0.000 description 4
- 229910052717 sulfur Inorganic materials 0.000 description 4
- 239000011593 sulfur Substances 0.000 description 4
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 230000008901 benefit Effects 0.000 description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 description 3
- 239000003610 charcoal Substances 0.000 description 3
- 150000001805 chlorine compounds Chemical class 0.000 description 3
- 238000001914 filtration Methods 0.000 description 3
- 244000144992 flock Species 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 230000001939 inductive effect Effects 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000012071 phase Substances 0.000 description 3
- 239000011941 photocatalyst Substances 0.000 description 3
- NLKNQRATVPKPDG-UHFFFAOYSA-M potassium iodide Chemical compound [K+].[I-] NLKNQRATVPKPDG-UHFFFAOYSA-M 0.000 description 3
- 239000012264 purified product Substances 0.000 description 3
- 229960000909 sulfur hexafluoride Drugs 0.000 description 3
- DDFHBQSCUXNBSA-UHFFFAOYSA-N 5-(5-carboxythiophen-2-yl)thiophene-2-carboxylic acid Chemical compound S1C(C(=O)O)=CC=C1C1=CC=C(C(O)=O)S1 DDFHBQSCUXNBSA-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- CPELXLSAUQHCOX-UHFFFAOYSA-M Bromide Chemical compound [Br-] CPELXLSAUQHCOX-UHFFFAOYSA-M 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- CTQNGGLPUBDAKN-UHFFFAOYSA-N O-Xylene Chemical compound CC1=CC=CC=C1C CTQNGGLPUBDAKN-UHFFFAOYSA-N 0.000 description 2
- 229910019142 PO4 Inorganic materials 0.000 description 2
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 239000007900 aqueous suspension Substances 0.000 description 2
- 239000002585 base Substances 0.000 description 2
- 230000003115 biocidal effect Effects 0.000 description 2
- 239000003139 biocide Substances 0.000 description 2
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- 238000006555 catalytic reaction Methods 0.000 description 2
- 150000005827 chlorofluoro hydrocarbons Chemical class 0.000 description 2
- 239000000084 colloidal system Substances 0.000 description 2
- 239000000356 contaminant Substances 0.000 description 2
- 230000006378 damage Effects 0.000 description 2
- PXBRQCKWGAHEHS-UHFFFAOYSA-N dichlorodifluoromethane Chemical compound FC(F)(Cl)Cl PXBRQCKWGAHEHS-UHFFFAOYSA-N 0.000 description 2
- 238000007598 dipping method Methods 0.000 description 2
- 238000005530 etching Methods 0.000 description 2
- 239000000706 filtrate Substances 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 150000002222 fluorine compounds Chemical class 0.000 description 2
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- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
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- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 2
- 239000003973 paint Substances 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 2
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- 101100215641 Aeromonas salmonicida ash3 gene Proteins 0.000 description 1
- 241001527902 Aratus Species 0.000 description 1
- DJHGAFSJWGLOIV-UHFFFAOYSA-K Arsenate3- Chemical compound [O-][As]([O-])([O-])=O DJHGAFSJWGLOIV-UHFFFAOYSA-K 0.000 description 1
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- 229910004664 Cerium(III) chloride Inorganic materials 0.000 description 1
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- 102100034742 Rotatin Human genes 0.000 description 1
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- 150000001447 alkali salts Chemical class 0.000 description 1
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- RLCOZMCCEKDUPY-UHFFFAOYSA-H molybdenum hexafluoride Chemical compound F[Mo](F)(F)(F)(F)F RLCOZMCCEKDUPY-UHFFFAOYSA-H 0.000 description 1
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- 229910052757 nitrogen Inorganic materials 0.000 description 1
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- 230000005855 radiation Effects 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000007420 reactivation Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- HYHCSLBZRBJJCH-UHFFFAOYSA-N sodium polysulfide Chemical compound [Na+].S HYHCSLBZRBJJCH-UHFFFAOYSA-N 0.000 description 1
- 229910052979 sodium sulfide Inorganic materials 0.000 description 1
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000009987 spinning Methods 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 230000000638 stimulation Effects 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- 229910021653 sulphate ion Inorganic materials 0.000 description 1
- 230000009182 swimming Effects 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- WEQHQGJDZLDFID-UHFFFAOYSA-J thorium(iv) chloride Chemical compound Cl[Th](Cl)(Cl)Cl WEQHQGJDZLDFID-UHFFFAOYSA-J 0.000 description 1
- NFACJZMKEDPNKN-UHFFFAOYSA-N trichlorfon Chemical compound COP(=O)(OC)C(O)C(Cl)(Cl)Cl NFACJZMKEDPNKN-UHFFFAOYSA-N 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000003466 welding Methods 0.000 description 1
- PCMOZDDGXKIOLL-UHFFFAOYSA-K yttrium chloride Chemical compound [Cl-].[Cl-].[Cl-].[Y+3] PCMOZDDGXKIOLL-UHFFFAOYSA-K 0.000 description 1
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- B60H3/00—Other air-treating devices
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- B60H3/0608—Filter arrangements in the air stream
- B60H3/0633—Filter arrangements in the air stream with provisions for regenerating or cleaning the filter element
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8659—Removing halogens or halogen compounds
- B01D53/8662—Organic halogen compounds
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J19/00—Chemical, physical or physico-chemical processes in general; Their relevant apparatus
- B01J19/08—Processes employing the direct application of electric or wave energy, or particle radiation; Apparatus therefor
- B01J19/12—Processes employing the direct application of electric or wave energy, or particle radiation; Apparatus therefor employing electromagnetic waves
- B01J19/122—Incoherent waves
- B01J19/123—Ultraviolet light
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01J19/00—Chemical, physical or physico-chemical processes in general; Their relevant apparatus
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- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/54—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/56—Platinum group metals
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
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- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/0215—Coating
- B01J37/0217—Pretreatment of the substrate before coating
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- B60H3/00—Other air-treating devices
- B60H3/06—Filtering
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion ; Methods of operation or control of catalytic converters
- F01N3/2086—Activating the catalyst by light, photo-catalysts
-
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- B01J2208/00—Processes carried out in the presence of solid particles; Reactors therefor
- B01J2208/00008—Controlling the process
- B01J2208/00017—Controlling the temperature
- B01J2208/00106—Controlling the temperature by indirect heat exchange
- B01J2208/00168—Controlling the temperature by indirect heat exchange with heat exchange elements outside the bed of solid particles
- B01J2208/00176—Controlling the temperature by indirect heat exchange with heat exchange elements outside the bed of solid particles outside the reactor
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- B01J2208/00008—Controlling the process
- B01J2208/00017—Controlling the temperature
- B01J2208/0053—Controlling multiple zones along the direction of flow, e.g. pre-heating and after-cooling
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- B01J2208/00—Processes carried out in the presence of solid particles; Reactors therefor
- B01J2208/00008—Controlling the process
- B01J2208/00592—Controlling the pH
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- B01J2219/00—Chemical, physical or physico-chemical processes in general; Their relevant apparatus
- B01J2219/18—Details relating to the spatial orientation of the reactor
- B01J2219/182—Details relating to the spatial orientation of the reactor horizontal
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- B60H3/00—Other air-treating devices
- B60H3/06—Filtering
- B60H2003/0675—Photocatalytic filters
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B60H3/00—Other air-treating devices
- B60H3/06—Filtering
- B60H2003/0691—Adsorption filters, e.g. activated carbon
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- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/30—Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]
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Abstract
ABSTRACT OF THE DISCLOSURE
The present invention relates to a method and pertinent apparatus for purifying gases, exhaust gases, vapors, and brines, which are contaminated with undesirable chemical substances or contain high concentrations of these substances, by means of photocatalytic reactions occurring on the surface of catalysts.
The catalysts are situated in a fixed or fluidized bed on catalyst carriers. In fluidized beds, the catalysts themselves can serve as catalyst carriers. The substrates to be purified are fed through a closed system which contains the catalyst carriers and catalysts.
In the fixed-bed catalytic method, the catalyst carrier/catalyst system continuously or discontinuously passes through a washing zone to remove the generated mineralization products.
The reaction is induced by shortwave photons of wavelengths between 250 and 400 nm.
The present invention relates to a method and pertinent apparatus for purifying gases, exhaust gases, vapors, and brines, which are contaminated with undesirable chemical substances or contain high concentrations of these substances, by means of photocatalytic reactions occurring on the surface of catalysts.
The catalysts are situated in a fixed or fluidized bed on catalyst carriers. In fluidized beds, the catalysts themselves can serve as catalyst carriers. The substrates to be purified are fed through a closed system which contains the catalyst carriers and catalysts.
In the fixed-bed catalytic method, the catalyst carrier/catalyst system continuously or discontinuously passes through a washing zone to remove the generated mineralization products.
The reaction is induced by shortwave photons of wavelengths between 250 and 400 nm.
Description
2 ~ ~ rrj r~
OESTE, Franz Dietrich Steibergstr. 4 D-6309 Munzenberg 2 Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and ~rines.
The present invention relates to a method and apparatus for purifying gases, exhaust gases, vapors, and brines, which are contaminated with undesirable chemical substances or contain high concentrations of these substances, by means of photocatalytic reactions occurring on the surface of catalysts.
The catalysts are situated on catalyst carriers in a fixed bed or in a fluidized bed. In fluidized beds, the catalysts themselves can serve as catalyst carriers. The substrates to be purified are fed through a closed system which contains the catalyst carriers and catalysts.
In the fixed-bed catalytic process, the catalyst carrier/catalyst system continuously or discontinuously passes through a washing zone to remove the generated mineralization products.
The reaction is induced by shortwave photons of wavelengths between 250 and 400 nm.
Endothermic chemical reactions require energy. Energy can be supplied in numerous ways. Frequently, photons of various wavelengths are employed.
Since these reactions occur at relatively low temperatures, catalysts are added to accelerate the reaction.
In the following, this combination of inducing chemical reactions by photons and increasing the speed of reactions by catalysts will be referred to as photocatalysis.
Photocatalyzed chemical reactions have been the sub~ect of increasing attention for some time. Applications have been sought for these reactions in the area of environmen~al protection.
, ,, . , ~, - "~. , '~ ' .
... ..
'.` ' .. ~ :
- 2 - 2~7~
In Environmental Sci. Technol. Vol. 17, No. 10 (1983) 828-31, for example, a reaction is described in which chloroform is degraded in an aqueous suspension of titanium dioxide by photoassisted, heterogeneous catalysis.
Chloroform is a main by-product occurring in the disinfecting chlorine treatment of drinking water and also, for example, water in swimming pools.
Chloroform is ascribed carcinogenic characteristics.
This method is applicable ~o aqueous suspensions with high particle content, known as slurries. A disadvantage of this method is the production of hydrochloric acid, which must be removed from the system.
European Patent Application 89100265.1 discloses a method and apparatus for the removal of hydrogen sulfide from exhaust gases using a titanium dioxide catalyst applied on the surface of a honeycomb support of activated charcoal, and ultraviolet radiation.
The activated charcoal adsorbs odorous compounds, such as H2S and scatoles, which are degraded by ultraviolet light. The method is a selective method and has the disadvantage that only part of the total surface can be utilized for the reaction.
In DOS 40 23 995.0, a method is disclosed in which pollutants are photocatalytically mineralized by a fixed-bed catalyst which is moved relative to the photon source.
Compared to other methods for the destruction of pollutants, such as incineration, this method has the advantage that it does not create additional environmental pollutants. These occur in incineration when auxiliary fuel is required, which usually results in the production of carbon dioxide.
The method described in the cited DOS patent does not require auxiliary fuel, even when the pollutant occurs in v~ry low concentrations, and is carried out at relatively low temperatures.
Liquid or solid mineralization products such as phosphoric and arsenic acid, however, can accumulate on the photocatalyst if pollutants are continually employed which, in addition to carbon, hydrogen, oxygen, and nitrogen, contain, e. g., halogens, sulfur, phosphorus, or arsenic, as well as pollutants and other wastes ~' , .: , : ;
2 ~
OESTE, Franz Dietrich Steibergstr. 4 D-6309 Munzenberg 2 Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and ~rines.
The present invention relates to a method and apparatus for purifying gases, exhaust gases, vapors, and brines, which are contaminated with undesirable chemical substances or contain high concentrations of these substances, by means of photocatalytic reactions occurring on the surface of catalysts.
The catalysts are situated on catalyst carriers in a fixed bed or in a fluidized bed. In fluidized beds, the catalysts themselves can serve as catalyst carriers. The substrates to be purified are fed through a closed system which contains the catalyst carriers and catalysts.
In the fixed-bed catalytic process, the catalyst carrier/catalyst system continuously or discontinuously passes through a washing zone to remove the generated mineralization products.
The reaction is induced by shortwave photons of wavelengths between 250 and 400 nm.
Endothermic chemical reactions require energy. Energy can be supplied in numerous ways. Frequently, photons of various wavelengths are employed.
Since these reactions occur at relatively low temperatures, catalysts are added to accelerate the reaction.
In the following, this combination of inducing chemical reactions by photons and increasing the speed of reactions by catalysts will be referred to as photocatalysis.
Photocatalyzed chemical reactions have been the sub~ect of increasing attention for some time. Applications have been sought for these reactions in the area of environmen~al protection.
, ,, . , ~, - "~. , '~ ' .
... ..
'.` ' .. ~ :
- 2 - 2~7~
In Environmental Sci. Technol. Vol. 17, No. 10 (1983) 828-31, for example, a reaction is described in which chloroform is degraded in an aqueous suspension of titanium dioxide by photoassisted, heterogeneous catalysis.
Chloroform is a main by-product occurring in the disinfecting chlorine treatment of drinking water and also, for example, water in swimming pools.
Chloroform is ascribed carcinogenic characteristics.
This method is applicable ~o aqueous suspensions with high particle content, known as slurries. A disadvantage of this method is the production of hydrochloric acid, which must be removed from the system.
European Patent Application 89100265.1 discloses a method and apparatus for the removal of hydrogen sulfide from exhaust gases using a titanium dioxide catalyst applied on the surface of a honeycomb support of activated charcoal, and ultraviolet radiation.
The activated charcoal adsorbs odorous compounds, such as H2S and scatoles, which are degraded by ultraviolet light. The method is a selective method and has the disadvantage that only part of the total surface can be utilized for the reaction.
In DOS 40 23 995.0, a method is disclosed in which pollutants are photocatalytically mineralized by a fixed-bed catalyst which is moved relative to the photon source.
Compared to other methods for the destruction of pollutants, such as incineration, this method has the advantage that it does not create additional environmental pollutants. These occur in incineration when auxiliary fuel is required, which usually results in the production of carbon dioxide.
The method described in the cited DOS patent does not require auxiliary fuel, even when the pollutant occurs in v~ry low concentrations, and is carried out at relatively low temperatures.
Liquid or solid mineralization products such as phosphoric and arsenic acid, however, can accumulate on the photocatalyst if pollutants are continually employed which, in addition to carbon, hydrogen, oxygen, and nitrogen, contain, e. g., halogens, sulfur, phosphorus, or arsenic, as well as pollutants and other wastes ~' , .: , : ;
2 ~
3 --consisting solely of these latter elements. The low reaction temperature, generally below 50C, does not allow these substances to evaporate. As a result, the photocatalytic function is increasingly inhibited, and the reaction finally s~ops completely.
There are several known methods for removing pollutants and contaminants from exhaust gases and other media in which they are undesirable.
These include purely physical methods such as adsorp~ion or absorption, or purely chemical methods such as chemisorption or incineration.
These methods, however, are frequently unsuitable for minerali~ing or removing complicated chemical compounds, such as sulfur hexafluoride, by economically or ecologically acceptable means.
These methods have other disadvantages as well. Physical sorption methods are limited by sorbent capacity. The loaded sorbent must either be disposed of, frequently as hazardous waste, or be desorbed, a process requiring large amounts of energy.
The alternative incineration methods, on the other hand, frequently lead to high expenditures for cleaning the exhaust gases of the pollutants and of the auxiliary fuel. The normally high incineration temperatures result in extremely high energy expenditures if the incineration warmth is not utilized.
All of the stated methods and apparatus in the art have certain disadvantages in their scope of application, service life, and the resulting total space-time yield, significantly reducing their cost-effectiveness.
Taking the shortcomings of other methods into consideration, it is the object of the present invention to provide a method and apparatus for carrying out the invention which circumvent the stated disadvantages, are more universally applicable, allow the resulting products to be easily removed from the system, and allow the mineralization of even difficult chemical substances, such as inert halogen-carbon compounds, halogenated hydrocarbons, or SF6.
The object of the present invention is realized by a method for the purification of gases, exhaust gases, vapors, and brines, `, , '. . : '' ' ' ' ' ' , ~ ' " ' _ 4 _ 2~
contaminated with or containing undesirable chemical substances, by means of photocatalytic reactions occurring on the surface of catalysts, wherein the substrate to be purified is fed through a physically closed system consisting of:
a) a catalyst carrier with a high specific surface relative to the material used, which is long-term resistant to chemical corrosion and shortwave light, and which shows the mechanical stability needed for mobile mechanical parts;
b) a catalyst applied to the catalyst carrier and consisting of at least one oxide and/or mixoxide with semiconductor behaviors mixed and/or loaded with a metal of the platinum series of the VIII group of the periodic table of chemical elements;
c) a catalyst applied to the catalyst carrier and consisting of at least one element of the lanthanides, actinides,and the IIIb group of the periodic table of chemical elements;
d) at least one source of shortwave light of wavelength from 250 to 400 nm, as a photon source;
e) at least one washing zone for the catalyst carrier in accordance with a), on which catalysts are applied in accordance with b) and c), through which the catalyst carrier is transported and treated with polar solvents.
The catalyst carriers consist of mats, knitted or comparable wovens or nonwovens, preferably in packets of stainless steel, titanium, tantalum, niobium, zirconium, hafnium, or metals of the VIII group of the periodic table of chemical elements, such as palladium or platinum. The surface of the catalyst carriers is roughened in order to increase the surface area and to improve the adhesion of the applied catalysts. The surface is roughened mechanically and/or chemically-oxidatively. Examples for chemical roughening are acidic etching and for oxidative roughening annealing in an oxidative medium. The catalyst carrier packets or bundles are fixed in frames, on glass plates or similar apparatus, - 5 ~
which consist of noncorroding materials and are resistant to shortwave light.
Porous materials in tubes, for example, can be used as catalyst carriers as well. The catalyst carriers can consist of thick porous tubes or porous sheets. The porous sheets can be joined to form sheet systems as in heat exchangers.
In special cases, particularly in cases of low oxidative media, the catalyst carrier can consist of porous carbon or carbon fibers.
Porous ceramics with zeolite structures or closed cell organic or inorganic polymer- or polycondensation materials can be used as catalyst carriers as well.
In the method of the present invention, the catalyst carriers occasionally serve as catalysts themselves, e. g., metals containing partially oxidized titanium or zirconium or etched precious metals containing platinum or palladium. Partially oxidized and etched metals have a very high specific surface and are therefore surface-active.
Catalysts are applied to the catalyst carriers and consist of semiconductor oxides mixed and/or loaded with a metal of the platinum series of the VIII group of the periodic table of chemical elements.
, The oxides are of the formula:
M20X~ and MlM20 x,where Ml - elements of the Ia, IIa and IIb group of the periodic table M2 - Ti, Zr, Hf, V, Nb, Ta, and those of thc IIIb group such as yttrium and scandium.
The platinum series consists primarily of palladium, platinum, rhodium, and ruthenium.
x - means a stechiometric or understechiometric value When chemical compounds are used which are extremely difficult to degrade, e. g., SF6 or halogen-carbon compounds containing various halogens, an additional catalytic component is added to the catalytic system consisting of a salt, usuallyas chlorides of a lanthanide and/or an actinide element. The chlorides are converted to oxides and applied to the catalyst carrier.
. . ` ' .
- - 6 ~ 2~ '2~
The degradation reaction employed in the method of the present invention is induced by shortwave light usually supplied by low-pressure quartz lamps. Normally, light sources with a wattage between 200 and 1000 W are used, depending on the size of the purification apparatus and the geometry of the light sources. The use of several light sources of low wattage is preferable to the application of a few light sources of high wattage, mainly to avoid heat build-up within the purification unit.
The method of the present invention can be employed not only in fixed-bed but also in fluidized-bed catalytic methods as well. In fluidized-bed methods, the catalyst is suspended in the reaction medium.
Fluidized-bed catalysis has the advantage over fixed-bed catalysis that higher concentrations of catalytic particles per unit of bed volume can be achieved. The catalytic fluidized bed, however, requires a relatively constant air or gas flow through the fluidized particle bed.
Occasionally, the flow rate of the reaction medium may be too high.
In these cases, particle mobilization is achieved by inducing vibrations in all or some of the fluidized-bed catalyst carriers.
This is achieved by inducing vibrations inductively or piezoelectrically and is inde~endent of the direc~ion of flow, which may be in or against the direction of acceleration under normal gravitational conditions or in a centrifuge.
To reduce noise emission, the vibrations within the fluidized bed may also be stimulated by an ultrasonic transmitter.
When the f low is conducted horizontally over or through a particle bed surface, it is possible to deposit the bed coating as a continuous surface.
The vibratory bed has an advantage over the fluid-dynamically stimulated f luidized bed in that the requirements placed on particle fractionation are less stringent. If the catalytic particles are at least partially on ferromagnetic catalyst carriers, moving lines of magnetic flux may be used as an additional particle stimulation method for mobile beds. The movement of the lines of magnetic flux forces the particles of the , : ', `. . ': ' '.:
`', ~' ,: ' ~. ' `
. , :. . . .. :: .,.:.: .:
. , ' .
catalytic bed to constantly rearrange themselves and, consequently, continuously present new surface areas to the photons.
The catalyst carrier and catalytic load are continuously or discontinuously washed to regenerate the catalysts, as in the fixed bed catalytic method. Washing is conducted with polar solvents, preferably with water.
The reactivation of the catalysts is improved if the washing medium contains oxidizing substances, for example, H202 or ozone.
The catalysts are washed according to various process principles.
For example, the catalyst carriers and catalysts are bathed, or dipped in a bath, or sprayed, or sprayed and centrifuged.
In most cases, the substances to be removed are highly soluble, inorganic compounds.
If the mineralization is unfavorable, due to the composition of the substrate's contaminant, the coating of the catalys~ may be less soluble. In these cases, but also to generally accelerate mineralization, an aid, such as water vapor, ammonia, or liquid ammonia, may be added to the purification substrate.
The washing of fluidized-bed catalysts is best conducted by exchanging the catalyst batch. Fluidized-bed catalytic methods are preferably employed when gases occur as sole mineralization products.
When the substrate gas consists, for example, of pure gas, air, oxygen-enriched air, and polluted water is sprayed into the substrate gas, the method becomes a purification method for liquid substances, in a reversal of the substrate admission in the purification method of the present invention.
In all, the method of the present invention is the method of choice for the special requirements of substrates which are to be purified.
A further object of the present invention was to provide apparatus with which the method may be carried out.
- '" ~
.~ .
This object was realized by apparatus for carrying out the various applications of the method as described, the apparatus consisting of the following principal components:
f) a closed housing of a corrosion-resistant material, equipped with inlet and outlet nozzles for the substrate and product of the method, as well as with bearings and clamps for the catalyst carriérs and catalysts, and with a source of shortwave light;
g) a frame to hold the catalyst carriers and catalysts;
h) an apparatus to move the catalyst carriers and catalysts within the housing in accordance with f);
and i) at least one source of shortwave light in the wavelength range from 250 to 400 nm.
Except for the fluidized-bed method, the housing according to f) contains a cavity for the bathing liquid, which is equipped with inlet and outlet nozzles for the bathing liquid.
The catalyst-containing ~arrier is held in a frame, cage, or is otherwise secured, and moved through the bath in the cavity in such a way that, as a minimum, the entire carrier passes through it~
Alternatively, the washing of the catalyst may be conducted by a spraying method. The spray drips into the cavity, from which it is removed or returned to the process by re-circulation.
Due to the long-term effectiveness of the catalysts, washing by bath or spraying may be conducted in intervals.
The frame g) frequently is a cylindrical body with a central axle, a cavity surrounding the axle, followed by a round container, which may be subdivided into pockets and which is connected to the axle on both sides, resulting in a closed container 14 whose outer 62 and inner 63 cylinder casings are constructed in such a manner .
- . , ,: ~ , ; - :
. - . ~ .. ,;, :
' ` . ' _ 9 _ 2.~7~
that they are easily permeable for gases and can easily contain and secure the catalyst carriers and catalysts.
The frame holding the catalyst carriers and catalysts may be constructed in various geometric forms, for example, a square object in a packet which ~ravels up and down within the housing in accordance with g) and is thereby submerged in the washing liquid.
When applying such variations of the method, it must be guaranteed that the purification process is interrupted during the washing process or that multiple systems are in service so the substrate to be purified is fed to an available purification unit by synchronized switching.
Frames are not required in the fluidized-bed method. The catalyst carriers and catalysts are suspended within the container and require a supporting base plate or drum which must be permeable for gases but impermeable for particulate matter.
The method can be conducted in reductive as well as in oxidative media, for example, when purifying extremely inert chlorofluorohydrocarbons. These compounds are best mineralized under oxygen-free conditions and in the presence of H2S, CS2, COS, or mixtures thereof. The presence of water and/or ammonia also promotes the reaction.
Other reductive agents which helps to eliminate halogens, are for example, dithiols, mercaptans, thiophenols and their alkali salts, sodium sulfide, and sodium polysulfide, which are introduced to the process as gases or, for example, as aqueous solutions.
By reversing these conditions, these sulfur compounds, if occurring as unwanted pollutants, can be eliminated by the method of the present invention. This is especially important, since these compounds are extremely odorous.
Nany gases contain significant amounts of the covalently bound pollutants as aerosols. In a variation of the method of the present invention, precipitation of these components can be promoted by connecting the catalyst fixed bed to a voltage differential. Depending on the geometry of the fixed bed, the backplate electrode may be either the housing ~) itself, or 1 0 ~ 3 r~ 7 ~ ~
appropriately positioned wires, or even an additional catalyst fixed bed, as shown in Fig. 3.
Surprisingly, the new method functions even if the aqueous phase, the bath or the washing liquid used to spray the catalyst, is polluted with organochemical substances. The pollutants are adsorbed from aqueous solution and adhesively bound by the catalyst carrier and the catalyst.
Even oil films on the surface of the water or substances dissolved in the aqueous solution, for example, are adsorbed by the catalyst fixed bed, appear in the gas phase, and are mineralized under the influence of the photons. This variation shows the applicability of the method for purifying extremely polluted waste water, which would be difficult by any other means.
Examples of the apparatus required for carrying out the method are illustrated in Figures 1 to 7.
Fig. 1. shows a standard apparatus. The hermetic enclosure of the reaction chamber 11 by the bath 12 and the side wall of the cylindrical container 14 forces the substrate to travel through the photon-irradiated 7 catalyst fixed bed 1. This is also where photocatalytic mineralization of undesirable substrate components occurs. The purified product leaves the purification unit 15 via the hollow axle 5.
The catalyst fixed bed and the catalysts are washed in bath 12 and freed of minerals, which are removed with the washing liquid via nozæle 10.
.
Fig. 2 shows the same apparatus in a vertical cross section along the middle axis.
Fig. 3 shows a variation of the apparatus for the purification of co~alently bound pollutants in aerosols.
Purification is best conducted with an electric field as described in Example 8.
Fig. 4 shows a variation of the apparatus for pollutants which ; are extremely difficult to eliminate. r~he apparatus is .
2~rt~
designed such that purification is conducted in two stages. The first purification stage occurs between chamber areas 34/51, and the second stage occurs betw~en chamber areas 42/52. The method is described in detail in Example 5.
ig. 5 shows a vertical cross section of the apparatus of Fig. 4.
ig. 6 shows a variation of the apparatus in which the washing liquid is admitted through the same inlet as the substrate to be purified. The catalyst carrier and catalyst are washed by spinning off the washing liquid as described in Example 9.
ig. 7 Shows an apparatus which uses fluidized-bed catalysts.
The applications of this new method are extremely diverse. ~he fixed-bed catalyst method is used in households for air purification as well as for flue gas dust collectors. In v~hicles, it is used for purifying circulated air and exhaust gases. In public buildings, e. g., schools, parking garages, and hospitals, it is used for purifying circulated air and emissions.
Fixed- and fluidized-bed catalytic methods are also employed in several other sectors, for example, in paint factories and paint shops, in glue factories and in glueing, and in the production of printing inks and in printing to remove solvent and softener vapors. They are also used in the chemical and pharmaceutical industries, in refineries, and in coking plants to remove all types of pollutants, employing as required a variation of the method of the present invention~ They are also used for occupational safety, for example, in welding.
Other applications are the decontamination of ground water and soil by abandoned pollutants or following accidents.
Further applications are the destruction of chlorofluorohydrocarbons, PCBs, or other environmental poisons, dangerous by-products of semiconductor production, such as ASH3, SiC14, SiHC13, SiH4, SF6, MoF6, the flue gases of viscose production, which contain CS2 and H2S, the black liquors occurring in cellulose production, and waste waters in electroplating shop~
tanneries and pesticide pollution.
, - 12 - 2~7~
The destxuction of gases for chemical warfare, such as LOST, or nerve gases which contain phosphorus are additional fields of application.
The method is also called for in clean-room technology, since a precleaning step would significantly reduce even residual traces of micro-particles.
The new method is a significant contribution to solving environmental pollution problems and is extremely energy-saving and cost-effective.
The following examples will demonstrate some of the capabilities of the method and its apparatus.
.
Posi~ions-Zahlen-Lis~e LiSl ol relere~3e~n~rnb~rs A~le casc 1I Sbch~ott - ker--vora I ¦¦ Antnclaet Applicanl rT-OES ?hotocatalytic method OESTE, Franz Dietr~Ah Posl 3enennunoiDtSl9nal~on and aDDaratus i _ 4 9 d~ e t -an s mi s s i on 1 ¦ cata~rs~ ed bed 50 l e~tei i nb- 10CK
51 ¦ ?u-e 3as chamDer, 1st sta3e 3 !!noto- 52 ! ~u~e ~as chamDer, 2nd sba~e
There are several known methods for removing pollutants and contaminants from exhaust gases and other media in which they are undesirable.
These include purely physical methods such as adsorp~ion or absorption, or purely chemical methods such as chemisorption or incineration.
These methods, however, are frequently unsuitable for minerali~ing or removing complicated chemical compounds, such as sulfur hexafluoride, by economically or ecologically acceptable means.
These methods have other disadvantages as well. Physical sorption methods are limited by sorbent capacity. The loaded sorbent must either be disposed of, frequently as hazardous waste, or be desorbed, a process requiring large amounts of energy.
The alternative incineration methods, on the other hand, frequently lead to high expenditures for cleaning the exhaust gases of the pollutants and of the auxiliary fuel. The normally high incineration temperatures result in extremely high energy expenditures if the incineration warmth is not utilized.
All of the stated methods and apparatus in the art have certain disadvantages in their scope of application, service life, and the resulting total space-time yield, significantly reducing their cost-effectiveness.
Taking the shortcomings of other methods into consideration, it is the object of the present invention to provide a method and apparatus for carrying out the invention which circumvent the stated disadvantages, are more universally applicable, allow the resulting products to be easily removed from the system, and allow the mineralization of even difficult chemical substances, such as inert halogen-carbon compounds, halogenated hydrocarbons, or SF6.
The object of the present invention is realized by a method for the purification of gases, exhaust gases, vapors, and brines, `, , '. . : '' ' ' ' ' ' , ~ ' " ' _ 4 _ 2~
contaminated with or containing undesirable chemical substances, by means of photocatalytic reactions occurring on the surface of catalysts, wherein the substrate to be purified is fed through a physically closed system consisting of:
a) a catalyst carrier with a high specific surface relative to the material used, which is long-term resistant to chemical corrosion and shortwave light, and which shows the mechanical stability needed for mobile mechanical parts;
b) a catalyst applied to the catalyst carrier and consisting of at least one oxide and/or mixoxide with semiconductor behaviors mixed and/or loaded with a metal of the platinum series of the VIII group of the periodic table of chemical elements;
c) a catalyst applied to the catalyst carrier and consisting of at least one element of the lanthanides, actinides,and the IIIb group of the periodic table of chemical elements;
d) at least one source of shortwave light of wavelength from 250 to 400 nm, as a photon source;
e) at least one washing zone for the catalyst carrier in accordance with a), on which catalysts are applied in accordance with b) and c), through which the catalyst carrier is transported and treated with polar solvents.
The catalyst carriers consist of mats, knitted or comparable wovens or nonwovens, preferably in packets of stainless steel, titanium, tantalum, niobium, zirconium, hafnium, or metals of the VIII group of the periodic table of chemical elements, such as palladium or platinum. The surface of the catalyst carriers is roughened in order to increase the surface area and to improve the adhesion of the applied catalysts. The surface is roughened mechanically and/or chemically-oxidatively. Examples for chemical roughening are acidic etching and for oxidative roughening annealing in an oxidative medium. The catalyst carrier packets or bundles are fixed in frames, on glass plates or similar apparatus, - 5 ~
which consist of noncorroding materials and are resistant to shortwave light.
Porous materials in tubes, for example, can be used as catalyst carriers as well. The catalyst carriers can consist of thick porous tubes or porous sheets. The porous sheets can be joined to form sheet systems as in heat exchangers.
In special cases, particularly in cases of low oxidative media, the catalyst carrier can consist of porous carbon or carbon fibers.
Porous ceramics with zeolite structures or closed cell organic or inorganic polymer- or polycondensation materials can be used as catalyst carriers as well.
In the method of the present invention, the catalyst carriers occasionally serve as catalysts themselves, e. g., metals containing partially oxidized titanium or zirconium or etched precious metals containing platinum or palladium. Partially oxidized and etched metals have a very high specific surface and are therefore surface-active.
Catalysts are applied to the catalyst carriers and consist of semiconductor oxides mixed and/or loaded with a metal of the platinum series of the VIII group of the periodic table of chemical elements.
, The oxides are of the formula:
M20X~ and MlM20 x,where Ml - elements of the Ia, IIa and IIb group of the periodic table M2 - Ti, Zr, Hf, V, Nb, Ta, and those of thc IIIb group such as yttrium and scandium.
The platinum series consists primarily of palladium, platinum, rhodium, and ruthenium.
x - means a stechiometric or understechiometric value When chemical compounds are used which are extremely difficult to degrade, e. g., SF6 or halogen-carbon compounds containing various halogens, an additional catalytic component is added to the catalytic system consisting of a salt, usuallyas chlorides of a lanthanide and/or an actinide element. The chlorides are converted to oxides and applied to the catalyst carrier.
. . ` ' .
- - 6 ~ 2~ '2~
The degradation reaction employed in the method of the present invention is induced by shortwave light usually supplied by low-pressure quartz lamps. Normally, light sources with a wattage between 200 and 1000 W are used, depending on the size of the purification apparatus and the geometry of the light sources. The use of several light sources of low wattage is preferable to the application of a few light sources of high wattage, mainly to avoid heat build-up within the purification unit.
The method of the present invention can be employed not only in fixed-bed but also in fluidized-bed catalytic methods as well. In fluidized-bed methods, the catalyst is suspended in the reaction medium.
Fluidized-bed catalysis has the advantage over fixed-bed catalysis that higher concentrations of catalytic particles per unit of bed volume can be achieved. The catalytic fluidized bed, however, requires a relatively constant air or gas flow through the fluidized particle bed.
Occasionally, the flow rate of the reaction medium may be too high.
In these cases, particle mobilization is achieved by inducing vibrations in all or some of the fluidized-bed catalyst carriers.
This is achieved by inducing vibrations inductively or piezoelectrically and is inde~endent of the direc~ion of flow, which may be in or against the direction of acceleration under normal gravitational conditions or in a centrifuge.
To reduce noise emission, the vibrations within the fluidized bed may also be stimulated by an ultrasonic transmitter.
When the f low is conducted horizontally over or through a particle bed surface, it is possible to deposit the bed coating as a continuous surface.
The vibratory bed has an advantage over the fluid-dynamically stimulated f luidized bed in that the requirements placed on particle fractionation are less stringent. If the catalytic particles are at least partially on ferromagnetic catalyst carriers, moving lines of magnetic flux may be used as an additional particle stimulation method for mobile beds. The movement of the lines of magnetic flux forces the particles of the , : ', `. . ': ' '.:
`', ~' ,: ' ~. ' `
. , :. . . .. :: .,.:.: .:
. , ' .
catalytic bed to constantly rearrange themselves and, consequently, continuously present new surface areas to the photons.
The catalyst carrier and catalytic load are continuously or discontinuously washed to regenerate the catalysts, as in the fixed bed catalytic method. Washing is conducted with polar solvents, preferably with water.
The reactivation of the catalysts is improved if the washing medium contains oxidizing substances, for example, H202 or ozone.
The catalysts are washed according to various process principles.
For example, the catalyst carriers and catalysts are bathed, or dipped in a bath, or sprayed, or sprayed and centrifuged.
In most cases, the substances to be removed are highly soluble, inorganic compounds.
If the mineralization is unfavorable, due to the composition of the substrate's contaminant, the coating of the catalys~ may be less soluble. In these cases, but also to generally accelerate mineralization, an aid, such as water vapor, ammonia, or liquid ammonia, may be added to the purification substrate.
The washing of fluidized-bed catalysts is best conducted by exchanging the catalyst batch. Fluidized-bed catalytic methods are preferably employed when gases occur as sole mineralization products.
When the substrate gas consists, for example, of pure gas, air, oxygen-enriched air, and polluted water is sprayed into the substrate gas, the method becomes a purification method for liquid substances, in a reversal of the substrate admission in the purification method of the present invention.
In all, the method of the present invention is the method of choice for the special requirements of substrates which are to be purified.
A further object of the present invention was to provide apparatus with which the method may be carried out.
- '" ~
.~ .
This object was realized by apparatus for carrying out the various applications of the method as described, the apparatus consisting of the following principal components:
f) a closed housing of a corrosion-resistant material, equipped with inlet and outlet nozzles for the substrate and product of the method, as well as with bearings and clamps for the catalyst carriérs and catalysts, and with a source of shortwave light;
g) a frame to hold the catalyst carriers and catalysts;
h) an apparatus to move the catalyst carriers and catalysts within the housing in accordance with f);
and i) at least one source of shortwave light in the wavelength range from 250 to 400 nm.
Except for the fluidized-bed method, the housing according to f) contains a cavity for the bathing liquid, which is equipped with inlet and outlet nozzles for the bathing liquid.
The catalyst-containing ~arrier is held in a frame, cage, or is otherwise secured, and moved through the bath in the cavity in such a way that, as a minimum, the entire carrier passes through it~
Alternatively, the washing of the catalyst may be conducted by a spraying method. The spray drips into the cavity, from which it is removed or returned to the process by re-circulation.
Due to the long-term effectiveness of the catalysts, washing by bath or spraying may be conducted in intervals.
The frame g) frequently is a cylindrical body with a central axle, a cavity surrounding the axle, followed by a round container, which may be subdivided into pockets and which is connected to the axle on both sides, resulting in a closed container 14 whose outer 62 and inner 63 cylinder casings are constructed in such a manner .
- . , ,: ~ , ; - :
. - . ~ .. ,;, :
' ` . ' _ 9 _ 2.~7~
that they are easily permeable for gases and can easily contain and secure the catalyst carriers and catalysts.
The frame holding the catalyst carriers and catalysts may be constructed in various geometric forms, for example, a square object in a packet which ~ravels up and down within the housing in accordance with g) and is thereby submerged in the washing liquid.
When applying such variations of the method, it must be guaranteed that the purification process is interrupted during the washing process or that multiple systems are in service so the substrate to be purified is fed to an available purification unit by synchronized switching.
Frames are not required in the fluidized-bed method. The catalyst carriers and catalysts are suspended within the container and require a supporting base plate or drum which must be permeable for gases but impermeable for particulate matter.
The method can be conducted in reductive as well as in oxidative media, for example, when purifying extremely inert chlorofluorohydrocarbons. These compounds are best mineralized under oxygen-free conditions and in the presence of H2S, CS2, COS, or mixtures thereof. The presence of water and/or ammonia also promotes the reaction.
Other reductive agents which helps to eliminate halogens, are for example, dithiols, mercaptans, thiophenols and their alkali salts, sodium sulfide, and sodium polysulfide, which are introduced to the process as gases or, for example, as aqueous solutions.
By reversing these conditions, these sulfur compounds, if occurring as unwanted pollutants, can be eliminated by the method of the present invention. This is especially important, since these compounds are extremely odorous.
Nany gases contain significant amounts of the covalently bound pollutants as aerosols. In a variation of the method of the present invention, precipitation of these components can be promoted by connecting the catalyst fixed bed to a voltage differential. Depending on the geometry of the fixed bed, the backplate electrode may be either the housing ~) itself, or 1 0 ~ 3 r~ 7 ~ ~
appropriately positioned wires, or even an additional catalyst fixed bed, as shown in Fig. 3.
Surprisingly, the new method functions even if the aqueous phase, the bath or the washing liquid used to spray the catalyst, is polluted with organochemical substances. The pollutants are adsorbed from aqueous solution and adhesively bound by the catalyst carrier and the catalyst.
Even oil films on the surface of the water or substances dissolved in the aqueous solution, for example, are adsorbed by the catalyst fixed bed, appear in the gas phase, and are mineralized under the influence of the photons. This variation shows the applicability of the method for purifying extremely polluted waste water, which would be difficult by any other means.
Examples of the apparatus required for carrying out the method are illustrated in Figures 1 to 7.
Fig. 1. shows a standard apparatus. The hermetic enclosure of the reaction chamber 11 by the bath 12 and the side wall of the cylindrical container 14 forces the substrate to travel through the photon-irradiated 7 catalyst fixed bed 1. This is also where photocatalytic mineralization of undesirable substrate components occurs. The purified product leaves the purification unit 15 via the hollow axle 5.
The catalyst fixed bed and the catalysts are washed in bath 12 and freed of minerals, which are removed with the washing liquid via nozæle 10.
.
Fig. 2 shows the same apparatus in a vertical cross section along the middle axis.
Fig. 3 shows a variation of the apparatus for the purification of co~alently bound pollutants in aerosols.
Purification is best conducted with an electric field as described in Example 8.
Fig. 4 shows a variation of the apparatus for pollutants which ; are extremely difficult to eliminate. r~he apparatus is .
2~rt~
designed such that purification is conducted in two stages. The first purification stage occurs between chamber areas 34/51, and the second stage occurs betw~en chamber areas 42/52. The method is described in detail in Example 5.
ig. 5 shows a vertical cross section of the apparatus of Fig. 4.
ig. 6 shows a variation of the apparatus in which the washing liquid is admitted through the same inlet as the substrate to be purified. The catalyst carrier and catalyst are washed by spinning off the washing liquid as described in Example 9.
ig. 7 Shows an apparatus which uses fluidized-bed catalysts.
The applications of this new method are extremely diverse. ~he fixed-bed catalyst method is used in households for air purification as well as for flue gas dust collectors. In v~hicles, it is used for purifying circulated air and exhaust gases. In public buildings, e. g., schools, parking garages, and hospitals, it is used for purifying circulated air and emissions.
Fixed- and fluidized-bed catalytic methods are also employed in several other sectors, for example, in paint factories and paint shops, in glue factories and in glueing, and in the production of printing inks and in printing to remove solvent and softener vapors. They are also used in the chemical and pharmaceutical industries, in refineries, and in coking plants to remove all types of pollutants, employing as required a variation of the method of the present invention~ They are also used for occupational safety, for example, in welding.
Other applications are the decontamination of ground water and soil by abandoned pollutants or following accidents.
Further applications are the destruction of chlorofluorohydrocarbons, PCBs, or other environmental poisons, dangerous by-products of semiconductor production, such as ASH3, SiC14, SiHC13, SiH4, SF6, MoF6, the flue gases of viscose production, which contain CS2 and H2S, the black liquors occurring in cellulose production, and waste waters in electroplating shop~
tanneries and pesticide pollution.
, - 12 - 2~7~
The destxuction of gases for chemical warfare, such as LOST, or nerve gases which contain phosphorus are additional fields of application.
The method is also called for in clean-room technology, since a precleaning step would significantly reduce even residual traces of micro-particles.
The new method is a significant contribution to solving environmental pollution problems and is extremely energy-saving and cost-effective.
The following examples will demonstrate some of the capabilities of the method and its apparatus.
.
Posi~ions-Zahlen-Lis~e LiSl ol relere~3e~n~rnb~rs A~le casc 1I Sbch~ott - ker--vora I ¦¦ Antnclaet Applicanl rT-OES ?hotocatalytic method OESTE, Franz Dietr~Ah Posl 3enennunoiDtSl9nal~on and aDDaratus i _ 4 9 d~ e t -an s mi s s i on 1 ¦ cata~rs~ ed bed 50 l e~tei i nb- 10CK
51 ¦ ?u-e 3as chamDer, 1st sta3e 3 !!noto- 52 ! ~u~e ~as chamDer, 2nd sba~e
4 !s~-a~ or ~ear disk 53 bath _ _ S !hoiiow a:~le 54 _ _ 6 !suDs~,-ate inlet noz~'e 55 h in, ~ig. 4 and 5 7 !sho-~~a~re lamD ~hoton source 56 8 !washin3 }icuid nieb 57 _ _ _ 9 !washinb l- luid outlet 58 10 ¦ba~h out'low _ _ 59 ~
ll !gas Dhase chamDer _ 60 su~70rtin~ a~;le 12 Icatal rs ~ashing bath 61 lain bea-in~_ 13 llsolat`-3 I'loat _ ____ 62 ou~,er c~rlinder casing lC ¦c~rlinc-ica7 catal~st `oed ca--ier 63 inner c-~rlinae- cas nb ~5 !a??ara-us hous nb _ 64 16 !DUre roduct ou let noz~le 65 midcle catal~rs~, bed 17 !su`ost-ate to `oe ~urified _ 66 SU`DStrate in_et no_z'e 13 !sa~a~r noz~les _ _ 67 hol ~ ow a;~le _ 19 !ca~alrs '-`~cec `oeà, ~i~. 3 _ 6a ^a-balyst Deds _ 20 !ca~a"s~, car~io- c~r`~inder 69 aua-tz glass ~'ates 21 IDnobor. source, Fi~,. 3 70 W lam~s 22 !rotatin~ ~ain a:cle _ _ 71 ?ure ~roduct crlamDe-23 !a?e-ture to 2nd Durif. sta~e 72 ure ?roduct ou~,iet 24 !wasr.i-.- liluid oub' et _ 73 a??aratus outer cas_n~, ~5 Ihousi.~ 3 74 ¦ a~ara-bus bot om _ _ . _ .
26 !r.e_ati-;e vol a~e source 75 ~asr.ing liauià O~ e-27 !oosi~, ~;e ~rol~a-e sou-Ao 76 rib-abinb base ?labe 2~ ! aO i a i .. ~las i c sl eeve_ 77 mesh oot~,om_?ia-bes ( '-i~s )_9 !s` i~ ^on_acT 78 catalys ~, fl uid -ed oe~
30 Is ^in~ ^on~ act 79 auarb~ ~lass ?ia~.e_ _ 31 !?U"e ?roduct out~ et 80 crude gas inlet 32 ! coc`~ - 'or cqta~rs ~ f :ced ~ed al ?ure as outlet 33 Isu-s t-a~e i n eT _ _ 82 _ _ 3 ¦c ube ~-as c:~lq `oer, ist ?uri;`. sta3e 83 1 _ ~
36 1 85 __ 37 ~aDerture to 2nd ~urif. sta~e B6 38 Is~_' 87 _ 39 IC _ai"ra_ -"asn- n,~- )aTbh 88 40 !-iasn ~ auia inlet ag - _ __ _ _ 41 l~asnin~- ~ icu__ ou-let si?non go 42 Ic~uce -_s ^:~la~^.o-r~ ~nc ~urif. staee 43 L~ n--a ii -_tion a c i nlet 44 !s -- n~ ~otor __ _ ~ S lonoton ,ou--c e ~ _ ~6 l~hoton. sourco ~7 !?U~oT~a~c~ outie~ Attr~rnuy Dr.EriChreimin 48~cente-inb d--ve rol'ers D-7881`Herrlschried, E x a m p 1 e Prepara~ion of the cataly3t carrier A three-dimensional, knitted wire mat of stainless steel with a layer thickness of 50 mm is cut into strips of 150 mm width and 1000 mm length.
The mesh is ca. 10 mm. The strips are used to form a hollow cylinder with the following dimensions: outer diameter ca. 30 cm, inner diameter ca. 20 cm, cylinder height ca. 15 cm.
The mat is held in shape by meshed stainless steel wires.
The cylinder is then blasted with grey cast iron blasting shot, mesh 0.2 to 0.4 mm, until the surface of the wire mat is well roughened, recognizable by the delustering of the wires.
Following this pretreatmen~, the diameter of the knitted wires is ca. 0.2 mm. The wire mesh is then washed and thoroughly dried.
The wire mesh is then dipped into a solution of soluble sodium, density 1.4 kg/l, and thoroughly wetted.
Short activated charcoal fibers with an average length of 1.0 to 3.5 mm, which are best produced by cutting fibrous webs of activated charcoal, are added to a 5% aqueous solution of citric acid. The charcoal fibers sediment completely in the citric acid solution and are then removed by decanting and filtration. The fibers are then dried to a constant weight at 70C.
The fibers are shaken through a sieve onto the wire mat, which has ~een wetted with the soluble sodium solution, until the surface of the wires is covered with the short charcoal fibers as comple~ely as possible. Prepared in this manner, the wire mat is then sprayed uniformly with a 5~ aqueous solution of soluble sodium, followed by a 5% aqueous solution of citric acid. It is then dried to a constant weight at 110C.
This method produces a thin silicate layer on the flock coating of charcoal fibers.
Subsequently, the wire mat is repeatedly dipped into a water bath to remove all soluble salts. The wire mat is then dxied to a constant wei~ht at 70C.
.
. ~ .
- ., ~;, ..: .; :
- 15 - 2~ 5~
Preparation of the ca~aly~t A suspension is prepared containing:
ll !gas Dhase chamDer _ 60 su~70rtin~ a~;le 12 Icatal rs ~ashing bath 61 lain bea-in~_ 13 llsolat`-3 I'loat _ ____ 62 ou~,er c~rlinder casing lC ¦c~rlinc-ica7 catal~st `oed ca--ier 63 inner c-~rlinae- cas nb ~5 !a??ara-us hous nb _ 64 16 !DUre roduct ou let noz~le 65 midcle catal~rs~, bed 17 !su`ost-ate to `oe ~urified _ 66 SU`DStrate in_et no_z'e 13 !sa~a~r noz~les _ _ 67 hol ~ ow a;~le _ 19 !ca~alrs '-`~cec `oeà, ~i~. 3 _ 6a ^a-balyst Deds _ 20 !ca~a"s~, car~io- c~r`~inder 69 aua-tz glass ~'ates 21 IDnobor. source, Fi~,. 3 70 W lam~s 22 !rotatin~ ~ain a:cle _ _ 71 ?ure ~roduct crlamDe-23 !a?e-ture to 2nd Durif. sta~e 72 ure ?roduct ou~,iet 24 !wasr.i-.- liluid oub' et _ 73 a??aratus outer cas_n~, ~5 Ihousi.~ 3 74 ¦ a~ara-bus bot om _ _ . _ .
26 !r.e_ati-;e vol a~e source 75 ~asr.ing liauià O~ e-27 !oosi~, ~;e ~rol~a-e sou-Ao 76 rib-abinb base ?labe 2~ ! aO i a i .. ~las i c sl eeve_ 77 mesh oot~,om_?ia-bes ( '-i~s )_9 !s` i~ ^on_acT 78 catalys ~, fl uid -ed oe~
30 Is ^in~ ^on~ act 79 auarb~ ~lass ?ia~.e_ _ 31 !?U"e ?roduct out~ et 80 crude gas inlet 32 ! coc`~ - 'or cqta~rs ~ f :ced ~ed al ?ure as outlet 33 Isu-s t-a~e i n eT _ _ 82 _ _ 3 ¦c ube ~-as c:~lq `oer, ist ?uri;`. sta3e 83 1 _ ~
36 1 85 __ 37 ~aDerture to 2nd ~urif. sta~e B6 38 Is~_' 87 _ 39 IC _ai"ra_ -"asn- n,~- )aTbh 88 40 !-iasn ~ auia inlet ag - _ __ _ _ 41 l~asnin~- ~ icu__ ou-let si?non go 42 Ic~uce -_s ^:~la~^.o-r~ ~nc ~urif. staee 43 L~ n--a ii -_tion a c i nlet 44 !s -- n~ ~otor __ _ ~ S lonoton ,ou--c e ~ _ ~6 l~hoton. sourco ~7 !?U~oT~a~c~ outie~ Attr~rnuy Dr.EriChreimin 48~cente-inb d--ve rol'ers D-7881`Herrlschried, E x a m p 1 e Prepara~ion of the cataly3t carrier A three-dimensional, knitted wire mat of stainless steel with a layer thickness of 50 mm is cut into strips of 150 mm width and 1000 mm length.
The mesh is ca. 10 mm. The strips are used to form a hollow cylinder with the following dimensions: outer diameter ca. 30 cm, inner diameter ca. 20 cm, cylinder height ca. 15 cm.
The mat is held in shape by meshed stainless steel wires.
The cylinder is then blasted with grey cast iron blasting shot, mesh 0.2 to 0.4 mm, until the surface of the wire mat is well roughened, recognizable by the delustering of the wires.
Following this pretreatmen~, the diameter of the knitted wires is ca. 0.2 mm. The wire mesh is then washed and thoroughly dried.
The wire mesh is then dipped into a solution of soluble sodium, density 1.4 kg/l, and thoroughly wetted.
Short activated charcoal fibers with an average length of 1.0 to 3.5 mm, which are best produced by cutting fibrous webs of activated charcoal, are added to a 5% aqueous solution of citric acid. The charcoal fibers sediment completely in the citric acid solution and are then removed by decanting and filtration. The fibers are then dried to a constant weight at 70C.
The fibers are shaken through a sieve onto the wire mat, which has ~een wetted with the soluble sodium solution, until the surface of the wires is covered with the short charcoal fibers as comple~ely as possible. Prepared in this manner, the wire mat is then sprayed uniformly with a 5~ aqueous solution of soluble sodium, followed by a 5% aqueous solution of citric acid. It is then dried to a constant weight at 110C.
This method produces a thin silicate layer on the flock coating of charcoal fibers.
Subsequently, the wire mat is repeatedly dipped into a water bath to remove all soluble salts. The wire mat is then dxied to a constant wei~ht at 70C.
.
. ~ .
- ., ~;, ..: .; :
- 15 - 2~ 5~
Preparation of the ca~aly~t A suspension is prepared containing:
5~ titanium dioxide powder, rutile type, mesh smaller than 0.1 mm 10% ethyl ti~anate, 3~ bentone swollen in xylol 0.5~ palladium, metal colloid 0.5~ rhodium, metal colloid and 81.0% xylol Depositing the catalyst on the catalyst carriex The catalyst suspension is deposited on the catalyst carrier by spraying or dipping and is dried at a temperature between 20C and 50C and a relative humidity of 50% to 95%. After the catalyst carrier and catalyst have been prepared as described, they are built into the apparatus components shown in Figs. l and 2, container 14.
Procedure Container 14 with catalyst carrier and catalyst l is mounted on a rotatable axle 60 supported by bearings 61 in a closed housing 15.
Catalyst carrier and catalyst form the catalyst fixed bed l.
The cylindrical container 14 is closed on both sides. The flow of substrate to be purified enters the purification unit (Figs. 1 and 2) of housing 15 via inlet nozzle 6. Since housing 15 is hermetically sealed, the substrate can reach the hollow axle 5 only by traversing the catalyst fixed bed l. The hollow axle 5 is also the outlet nozzle through which the substrate lea~es the purification unit as a purified product.
During the reaction, the catalyst fixed bed 1 is activated by several 200 W low pressure quartz lamps 7. The cylinder (container) 14 is continually rotated on cylinder axle 60 during the work phase. The axle 60 is drtven by motor 3 via hollow axle 5 and strap or gear disk 4.
During the work phase, the rotation dips the complete casing of the catalyst fixed bed into bath 12, which in this case is a water bath and is situated in the lower section of housing 15. The wash water enters the bath by inlet 8 at a rate of ca. 2 to 5 l/h.
,, .
r '' ~
~ter it is loaded with the mineralization products, it is removed from the bath via outlet 9.
In the reaction area of the quartz lamps 7, the surface of the bath is covered with isolating floats 13 to minimize evaporation and heating. Container 14 is turned at a speed of ca. 0.5 to 1.~ times per hour.
Tap water, but preferably water from an ion exchanger, is used as the washing liquid.
The process operates as follows:
An air stream is adjusted to a relative humidity of ca. 90% by feeding it through a tank of cooled water at a rate of 0.3 l/s.
At a rate of Q.l l/s, an additional stream of air is fed through a 2 liter washing flask roughly half-filled with a solution of various biocide substances. The biocide solution is of the following composition:
3 n % profenofos (0-ethyl-S-propyl-0-(2-chloro-4-bromphenyl)-thiophosphate; CllH15BrC103PS), 25~ chlorofos ~0,0-dimethyl-2,2,2-trichloro-1-hydroxy-ethane phosphate; C4H8C1304P), 5% cacodyl oxide (bis(dimethyl arsyl)oxide; As2(CH3)40), 25~ demeton-S (O,O-diethyl-S-(ethyl thio)ethyl thiophosphate;
C8H1903PS2) l 15% fluoro acetic acid-n-butyl ester (C6H11F02).
The two air streams are mixed with a static mixer and fed through the apparatus shown in Figs. 1 and 2. A defined aliquot of the gas stream fed through the catalyst fixed bed is diverted for analysis and burned in an oxyhydrogen gas flame. The resulting gas is condensed in a quartz cooler such that the condensate drips from the cooler into a diluted hydrogen peroxide solution. The fluoride, bromide, sulphate, phosphate and arsenate content. of the hydrogen peroxide solution is analyzed at two-hour intervals.
The solution contains hydrogen peroxide and a small amount of potassium iodide.
;: ., , :,,, , '' . ~ .: ' . .:
:. . ,,., ... ;.
- 17 ~
Even after the experiment was conducted continually for two weeks, none of the ions mentioned abo~e was detected in the hydrogen peroxide solution.
E x a m p 1 e 2 (Comparative example) The process is conducted exactly as described in Example 1, except that the catalyst is not washed. Pollutants were detected in the emissions after only 24 hours reaction time.
E x a m p 1 e 3 The process is conducted as described in Example 1, but the catalyst is washed not by bathing but rather by spraying the catalyst and catalyst carrier from the inside of container 14.
The washing liquid is removed through outlet 10. Container 14 is rotates at a speed of 300 to 1500 rpm during the washing method.
The washing is conducted discontinuously at intervals of 2 to 24 hours depending on the pollutant content of the substrate to be purified.
The resulting emissions are of the same quality as in Example 1.
E x a m p 1 e 4 The process is conducted exactly as described in Example 1, except that the catalyst is washed discontinuously. Bath 12 is filled for 15 minutes every two hours. The washing liquid is then removed.
The same good results were achieved as in Example 1.
E x a m p 1 e 5 Preparation of the catalyst carrier and catalyst A 20 mm thick, stainless steel knitted mat is cut into strips of 38 cm length and 4 cm width and roughened by corundum streams. The -, . ' ~ ::' ' .
- ~' :, ' - 18 2~
roughened stainless steel strips are treated with soluble sodium as in Example 1.
1.5 kg short aluminum oxide fibers with an average length of 1 to 3 mm and a diameter of 0.1 mm are stirred into a solution of 75 g thorium tetrachloride, 30 g cerium trichloride and lS g yttrium trichloride in 3 1 of water.
The solution is then neutralized by adding sodium hydroxide. The chlorides are converted into hydroxides and precipitate on the surface of the aluminum oxide fibers.
The applied fibers are removed by filtration, neutralized by washing, and dried.
The dry fibers are fluidized by a vertical air stream and the stainless steel knitted mat, which was wetted by treatment with soluble sodium, is flock coated by dipping into the shor~ fiber fluidized bed.
A high fiber density is achieved by applying a relatively high voltage of 5 kV to the stainless steel knitted strips during flock coating.
Immediately thereafter, the coated strips are dried to a constant weight in a CO2 atmosphere at room temperature. ThPy are then dried to a constant weight in a nitrogen atmosphere while the temperature is gradually increased to 400C. This temperature is maintained for two hours.
.~
The resulting strips are freed of alkali carbonates by washing and dried.
Subsequently, the prepared catalyst carrier is coated and fixed with palladium- and rhodium-doped titanium dioxide, as described in Example 1.
The resulting catalyst carriers and catalysts are mounted in the 64 pockets 32 of the catalyst carrier cylinder 20 as shown in Figs. 4 and 5. Cylinder 20 is then mounted in housing 55.
Cylinder 20 is mounted in chamber housing 55 such that sections of the cylinder are simultaneously in both of the chambers while the cylinder rotates.
;, , : ~
~, ' ~, '.
_ 19 ~
Cylinder 20 divides each of the two chambers 34/51 and 42/52 into two sections, the substrate section and the product section.
Cylinder 20 rota~es counterclockwise at a speed of 0.5 rpm and is driven eccentrically by the interconnected supporting rollers 48.
Procedure Nitrogen containing lO00 ppm sulfur hexafluoride, 5000 ppm carbon disulfide, 10000 ppm ammonia, and 20 g/m3 water vapor is fed into the chamber 34 via substrate inlet nozzle 33 at a rate of 0.3 l/s and a temperature of 23C.
The quartz lamps 45 and 46 on both sides of the chamber are turned on.
The photon emission maximum i5 between 300 and 400 nm.
The gas is fed through catalyst bed 62, where practically all pollutants are converted to elementary sulfur, ammonium fluoride, and carbon dioxide.
The resulting sulfur and ammonium fluoride remain on the catalyst.
The gas is then fed through aperture 37 into chamber 42 where, at a temperature of 20C, it is mixed with air which enters ~y inlet 43 at a rate of 0.3 lts and whose relative humidity has been adjusted to 100% at a temperature of 25C.
The gases are stirred by ro~or 44.
~ithout a change in photon conditions, the gas mixture is fed through catalyst bed 62 into chamber 52.
The gas reaching chamber 52 does not contain sulfur dioxide or any other pollutants. Residual pollutants, as well as the elementary sulfur on the catalyst, are converted to ammonium sulfate and ammonium hydrogen sulfate in the catalyst fixed bed of chamber areas 42/52. The purified product is removed from the purification unit by outlet 47.
The catalyst bed is washed continuously while moving through bath 63. The washing liquid enters upper section 39 of the bath by inlet 40 at a rate of 2 l/h, is fed through the catalyst bed where it removes mineralization products and is collected in lower section 53 of the bath.
~ ' - - 20 ~
The washing method removes mineralized salts, such as fluorides and sulfates. The resulting washing liquid is removed from the purification unit by siphon 41. Leveling locks 50 are regulated by the height of the siphon.
The ammonia content of the washing liquid is monitored via the pH-value, which varies between 6.5 and 7.5.
The seals 38 minimize gas leakage between the chambers.
.
- Waste water processing Milk of lime is added to the waste water. The resulting sulfates and fluorides precipitate as gypsom and fluorspar.
Subsequently, the waste water is stripped in a packed column using air in a counterflow system. The stripping air, which contains ammonia, is recycled via aperture 37 and is reintroduced to the process in chamber 42.
The precipitated calcium salts are removed by filtration and disposed of. The filtrate can be used as service water.
In this manner, extremely dangerous chemical substances are converted to harmless mineral salts.
E x a m p 1 e 6 As in Example 5, but with the following substrate composition:
500 ppm bromtrifluoro methane (halon), 200 ppm difluoro-dichloro methane instead of sulfur hexafluoride, and 5000 ppm H2S instead of carbon disulfide.
More than 95~ of the covalently bound halogens are mineralized to halogenides.
The waste water filtrate cannot be used as service water, since it contains calcium chloride and bromide.
~ :,...
.
- 21 - 2~
E x a m p 1 e 7 As in Example 5, except that a knitted mat of -titanium wire, preferably roughened, and of less than 0.5 mm diameter is used instead of a stainless steel mat.
The knitted mat is annealed in oxygen, resulting in a titanium dioxide layer on the surface of the wires, which supplies the required catalytic properties in this process.
Subsequently, the wire mat is dopPd with one or a mixture of the platinum metals and/or oxidized compounds of the elements or their mixtures from the lanthanide group or yttrium or the actinide group, leading to the same good results.
E x a m p 1 e 8 Nany gases contain significant amounts of the covalently bound pollutants as aerosols. For the precipitation of these components, it is advantageous to connect the photocatalyst fixed bed to a voltage differential. Depending on the geometry of the fixed bed, the bac~plate electrode may be either the housing itself, appropriately positioned wires, or even an additional catalyst fixed bed.
Fig~ 3 shows the geometry of three catalyst fixed beds 19, 65, which rotate around a common axle 22 within housing 25. ~oth external catalyst beds are connected electrically with conductive matal axle 22 and, via sliding contact 29, positive voltage source 27.
Central catalyst bed 65 is isolated from metal axle 22 by plastic sleeve 28 and receives a negative charge via sliding contact 30 from voltage source 26.
Two photon sources 21 are mounted rigidly between rotating catalyst beds 19, 65.
Spray nozzles 18 enrich the substrate, which enters the purification unit via 17, with an aerosol of washing liquid.
The rotational speed of the catalyst beds is variable between 10 and 500 rpm.
- 22 ~ 2 ~ 7~ ~
In intervals, rotational speed is increased to maximum to spin off washing liquid during washing.
Subsequently, the spun-off washing liquid is removed from the apparatus by outlet 24. ~he purified gas is removed by outlet 31.
5000 to 30,000 V is the ~est voltage range ~or s~ripping aerosols.
The catalyst carriers are prepared according to Examples 1 and 5.
E x a m p l e 9 Fig. 6 shows a further variation of the method using aerosols.
The substrate - polluted gas - is fed through inlet 66, hollow axle 67, and catalyst beds 68.
Spray nozzle 18 enriches the substrate with an aerosol of washing liquid. The catalyst beds are mounted between disk-shaped, round quart~ glass plates 69, which are securely fastened to the hollow axle.
The hollow axle is permeable for gases in the catalyst bed section between the quartz glass plates.
The hollow axle and, consequently, the catalyst bed are turned by a motor and drive unit 4, as in Example 8.
W lamps 70, the photon sources, are located between the catalyst beds.
The purified substrate is fed into chamber 71 and removed from the unit as a pure product by outlet 72.
A filled gas washer is mounted downstream of the purification unit to strip aerosols.
The washing liquid aerosol aggregates and coalesces within the catalyst fixed bed, is spun to wall 73 of the unit, collects in bottom section 74, and is removed from the apparatus by outlet 75.
E x a m p l e 10 A variation of Example 9 is to secure the photocatalyst fixed bed by a tight, transparent housing. The catalyst is secured within .
.,. ..~ ..
.
- 23 ~ 2~7~
glass capillaries. This is achieved by applying the catalyst to the glass walls or pores of the capillaries.
When employing wide capillaries with diameters of ca. 1 mm and larger, the catalyst particles are applied by pouring.
Previous etching improves the adhesion of the catalyst to the glass surface.
E x a m p 1 e 11 The apparatus can also serve as a waste water purification unit if, as in Example 9, the spray nozzle is fed with water to be purified and inlet 66 is fed with clean air~
;' ' '
Procedure Container 14 with catalyst carrier and catalyst l is mounted on a rotatable axle 60 supported by bearings 61 in a closed housing 15.
Catalyst carrier and catalyst form the catalyst fixed bed l.
The cylindrical container 14 is closed on both sides. The flow of substrate to be purified enters the purification unit (Figs. 1 and 2) of housing 15 via inlet nozzle 6. Since housing 15 is hermetically sealed, the substrate can reach the hollow axle 5 only by traversing the catalyst fixed bed l. The hollow axle 5 is also the outlet nozzle through which the substrate lea~es the purification unit as a purified product.
During the reaction, the catalyst fixed bed 1 is activated by several 200 W low pressure quartz lamps 7. The cylinder (container) 14 is continually rotated on cylinder axle 60 during the work phase. The axle 60 is drtven by motor 3 via hollow axle 5 and strap or gear disk 4.
During the work phase, the rotation dips the complete casing of the catalyst fixed bed into bath 12, which in this case is a water bath and is situated in the lower section of housing 15. The wash water enters the bath by inlet 8 at a rate of ca. 2 to 5 l/h.
,, .
r '' ~
~ter it is loaded with the mineralization products, it is removed from the bath via outlet 9.
In the reaction area of the quartz lamps 7, the surface of the bath is covered with isolating floats 13 to minimize evaporation and heating. Container 14 is turned at a speed of ca. 0.5 to 1.~ times per hour.
Tap water, but preferably water from an ion exchanger, is used as the washing liquid.
The process operates as follows:
An air stream is adjusted to a relative humidity of ca. 90% by feeding it through a tank of cooled water at a rate of 0.3 l/s.
At a rate of Q.l l/s, an additional stream of air is fed through a 2 liter washing flask roughly half-filled with a solution of various biocide substances. The biocide solution is of the following composition:
3 n % profenofos (0-ethyl-S-propyl-0-(2-chloro-4-bromphenyl)-thiophosphate; CllH15BrC103PS), 25~ chlorofos ~0,0-dimethyl-2,2,2-trichloro-1-hydroxy-ethane phosphate; C4H8C1304P), 5% cacodyl oxide (bis(dimethyl arsyl)oxide; As2(CH3)40), 25~ demeton-S (O,O-diethyl-S-(ethyl thio)ethyl thiophosphate;
C8H1903PS2) l 15% fluoro acetic acid-n-butyl ester (C6H11F02).
The two air streams are mixed with a static mixer and fed through the apparatus shown in Figs. 1 and 2. A defined aliquot of the gas stream fed through the catalyst fixed bed is diverted for analysis and burned in an oxyhydrogen gas flame. The resulting gas is condensed in a quartz cooler such that the condensate drips from the cooler into a diluted hydrogen peroxide solution. The fluoride, bromide, sulphate, phosphate and arsenate content. of the hydrogen peroxide solution is analyzed at two-hour intervals.
The solution contains hydrogen peroxide and a small amount of potassium iodide.
;: ., , :,,, , '' . ~ .: ' . .:
:. . ,,., ... ;.
- 17 ~
Even after the experiment was conducted continually for two weeks, none of the ions mentioned abo~e was detected in the hydrogen peroxide solution.
E x a m p 1 e 2 (Comparative example) The process is conducted exactly as described in Example 1, except that the catalyst is not washed. Pollutants were detected in the emissions after only 24 hours reaction time.
E x a m p 1 e 3 The process is conducted as described in Example 1, but the catalyst is washed not by bathing but rather by spraying the catalyst and catalyst carrier from the inside of container 14.
The washing liquid is removed through outlet 10. Container 14 is rotates at a speed of 300 to 1500 rpm during the washing method.
The washing is conducted discontinuously at intervals of 2 to 24 hours depending on the pollutant content of the substrate to be purified.
The resulting emissions are of the same quality as in Example 1.
E x a m p 1 e 4 The process is conducted exactly as described in Example 1, except that the catalyst is washed discontinuously. Bath 12 is filled for 15 minutes every two hours. The washing liquid is then removed.
The same good results were achieved as in Example 1.
E x a m p 1 e 5 Preparation of the catalyst carrier and catalyst A 20 mm thick, stainless steel knitted mat is cut into strips of 38 cm length and 4 cm width and roughened by corundum streams. The -, . ' ~ ::' ' .
- ~' :, ' - 18 2~
roughened stainless steel strips are treated with soluble sodium as in Example 1.
1.5 kg short aluminum oxide fibers with an average length of 1 to 3 mm and a diameter of 0.1 mm are stirred into a solution of 75 g thorium tetrachloride, 30 g cerium trichloride and lS g yttrium trichloride in 3 1 of water.
The solution is then neutralized by adding sodium hydroxide. The chlorides are converted into hydroxides and precipitate on the surface of the aluminum oxide fibers.
The applied fibers are removed by filtration, neutralized by washing, and dried.
The dry fibers are fluidized by a vertical air stream and the stainless steel knitted mat, which was wetted by treatment with soluble sodium, is flock coated by dipping into the shor~ fiber fluidized bed.
A high fiber density is achieved by applying a relatively high voltage of 5 kV to the stainless steel knitted strips during flock coating.
Immediately thereafter, the coated strips are dried to a constant weight in a CO2 atmosphere at room temperature. ThPy are then dried to a constant weight in a nitrogen atmosphere while the temperature is gradually increased to 400C. This temperature is maintained for two hours.
.~
The resulting strips are freed of alkali carbonates by washing and dried.
Subsequently, the prepared catalyst carrier is coated and fixed with palladium- and rhodium-doped titanium dioxide, as described in Example 1.
The resulting catalyst carriers and catalysts are mounted in the 64 pockets 32 of the catalyst carrier cylinder 20 as shown in Figs. 4 and 5. Cylinder 20 is then mounted in housing 55.
Cylinder 20 is mounted in chamber housing 55 such that sections of the cylinder are simultaneously in both of the chambers while the cylinder rotates.
;, , : ~
~, ' ~, '.
_ 19 ~
Cylinder 20 divides each of the two chambers 34/51 and 42/52 into two sections, the substrate section and the product section.
Cylinder 20 rota~es counterclockwise at a speed of 0.5 rpm and is driven eccentrically by the interconnected supporting rollers 48.
Procedure Nitrogen containing lO00 ppm sulfur hexafluoride, 5000 ppm carbon disulfide, 10000 ppm ammonia, and 20 g/m3 water vapor is fed into the chamber 34 via substrate inlet nozzle 33 at a rate of 0.3 l/s and a temperature of 23C.
The quartz lamps 45 and 46 on both sides of the chamber are turned on.
The photon emission maximum i5 between 300 and 400 nm.
The gas is fed through catalyst bed 62, where practically all pollutants are converted to elementary sulfur, ammonium fluoride, and carbon dioxide.
The resulting sulfur and ammonium fluoride remain on the catalyst.
The gas is then fed through aperture 37 into chamber 42 where, at a temperature of 20C, it is mixed with air which enters ~y inlet 43 at a rate of 0.3 lts and whose relative humidity has been adjusted to 100% at a temperature of 25C.
The gases are stirred by ro~or 44.
~ithout a change in photon conditions, the gas mixture is fed through catalyst bed 62 into chamber 52.
The gas reaching chamber 52 does not contain sulfur dioxide or any other pollutants. Residual pollutants, as well as the elementary sulfur on the catalyst, are converted to ammonium sulfate and ammonium hydrogen sulfate in the catalyst fixed bed of chamber areas 42/52. The purified product is removed from the purification unit by outlet 47.
The catalyst bed is washed continuously while moving through bath 63. The washing liquid enters upper section 39 of the bath by inlet 40 at a rate of 2 l/h, is fed through the catalyst bed where it removes mineralization products and is collected in lower section 53 of the bath.
~ ' - - 20 ~
The washing method removes mineralized salts, such as fluorides and sulfates. The resulting washing liquid is removed from the purification unit by siphon 41. Leveling locks 50 are regulated by the height of the siphon.
The ammonia content of the washing liquid is monitored via the pH-value, which varies between 6.5 and 7.5.
The seals 38 minimize gas leakage between the chambers.
.
- Waste water processing Milk of lime is added to the waste water. The resulting sulfates and fluorides precipitate as gypsom and fluorspar.
Subsequently, the waste water is stripped in a packed column using air in a counterflow system. The stripping air, which contains ammonia, is recycled via aperture 37 and is reintroduced to the process in chamber 42.
The precipitated calcium salts are removed by filtration and disposed of. The filtrate can be used as service water.
In this manner, extremely dangerous chemical substances are converted to harmless mineral salts.
E x a m p 1 e 6 As in Example 5, but with the following substrate composition:
500 ppm bromtrifluoro methane (halon), 200 ppm difluoro-dichloro methane instead of sulfur hexafluoride, and 5000 ppm H2S instead of carbon disulfide.
More than 95~ of the covalently bound halogens are mineralized to halogenides.
The waste water filtrate cannot be used as service water, since it contains calcium chloride and bromide.
~ :,...
.
- 21 - 2~
E x a m p 1 e 7 As in Example 5, except that a knitted mat of -titanium wire, preferably roughened, and of less than 0.5 mm diameter is used instead of a stainless steel mat.
The knitted mat is annealed in oxygen, resulting in a titanium dioxide layer on the surface of the wires, which supplies the required catalytic properties in this process.
Subsequently, the wire mat is dopPd with one or a mixture of the platinum metals and/or oxidized compounds of the elements or their mixtures from the lanthanide group or yttrium or the actinide group, leading to the same good results.
E x a m p 1 e 8 Nany gases contain significant amounts of the covalently bound pollutants as aerosols. For the precipitation of these components, it is advantageous to connect the photocatalyst fixed bed to a voltage differential. Depending on the geometry of the fixed bed, the bac~plate electrode may be either the housing itself, appropriately positioned wires, or even an additional catalyst fixed bed.
Fig~ 3 shows the geometry of three catalyst fixed beds 19, 65, which rotate around a common axle 22 within housing 25. ~oth external catalyst beds are connected electrically with conductive matal axle 22 and, via sliding contact 29, positive voltage source 27.
Central catalyst bed 65 is isolated from metal axle 22 by plastic sleeve 28 and receives a negative charge via sliding contact 30 from voltage source 26.
Two photon sources 21 are mounted rigidly between rotating catalyst beds 19, 65.
Spray nozzles 18 enrich the substrate, which enters the purification unit via 17, with an aerosol of washing liquid.
The rotational speed of the catalyst beds is variable between 10 and 500 rpm.
- 22 ~ 2 ~ 7~ ~
In intervals, rotational speed is increased to maximum to spin off washing liquid during washing.
Subsequently, the spun-off washing liquid is removed from the apparatus by outlet 24. ~he purified gas is removed by outlet 31.
5000 to 30,000 V is the ~est voltage range ~or s~ripping aerosols.
The catalyst carriers are prepared according to Examples 1 and 5.
E x a m p l e 9 Fig. 6 shows a further variation of the method using aerosols.
The substrate - polluted gas - is fed through inlet 66, hollow axle 67, and catalyst beds 68.
Spray nozzle 18 enriches the substrate with an aerosol of washing liquid. The catalyst beds are mounted between disk-shaped, round quart~ glass plates 69, which are securely fastened to the hollow axle.
The hollow axle is permeable for gases in the catalyst bed section between the quartz glass plates.
The hollow axle and, consequently, the catalyst bed are turned by a motor and drive unit 4, as in Example 8.
W lamps 70, the photon sources, are located between the catalyst beds.
The purified substrate is fed into chamber 71 and removed from the unit as a pure product by outlet 72.
A filled gas washer is mounted downstream of the purification unit to strip aerosols.
The washing liquid aerosol aggregates and coalesces within the catalyst fixed bed, is spun to wall 73 of the unit, collects in bottom section 74, and is removed from the apparatus by outlet 75.
E x a m p l e 10 A variation of Example 9 is to secure the photocatalyst fixed bed by a tight, transparent housing. The catalyst is secured within .
.,. ..~ ..
.
- 23 ~ 2~7~
glass capillaries. This is achieved by applying the catalyst to the glass walls or pores of the capillaries.
When employing wide capillaries with diameters of ca. 1 mm and larger, the catalyst particles are applied by pouring.
Previous etching improves the adhesion of the catalyst to the glass surface.
E x a m p 1 e 11 The apparatus can also serve as a waste water purification unit if, as in Example 9, the spray nozzle is fed with water to be purified and inlet 66 is fed with clean air~
;' ' '
Claims (30)
PROPERTY OR PRIVILEGE IS CLAIMED ARE DEFINED AS FOLLOWS:
1. Method for purifying gases, exhaust gases, vapors and brines, which are contaminated with or contain undesirable chemical substances, by means of photocatalytic reactions occurring on the surface of catalysts, wherein the substrates to be purified are fed through a physically closed system consisting of:
a) a catalyst carrier with a high specific surface relative to the material used, which is long-term resistant to chemical corrosion and shortwave light, and which shows the mechanical stability needed for mobile mechanical parts;
b) a catalyst, which is applied to said catalyst carrier, and which consists of at least one oxide and/or mixoxide with semiconductor behaviors mixed and/or loaded with at least one metal of the platinum series of the VIII group of the periodic cable of chemical elements;
c) a catalyst, which is applied to said catalyst carrier, and which consists of at least one element of the lanthanides, actinides,and the IIIb group of the periodic table of chemical elements;
d) at least one source of shortwave light of wavelengths from 250 to 400 nm, as a photon source;
e) at least one washing zone for said catalyst carrier in accordance with a), on which catalysts are applied in accordance with b) and c), through which said catalyst carrier is transported and treated with polar solvents
a) a catalyst carrier with a high specific surface relative to the material used, which is long-term resistant to chemical corrosion and shortwave light, and which shows the mechanical stability needed for mobile mechanical parts;
b) a catalyst, which is applied to said catalyst carrier, and which consists of at least one oxide and/or mixoxide with semiconductor behaviors mixed and/or loaded with at least one metal of the platinum series of the VIII group of the periodic cable of chemical elements;
c) a catalyst, which is applied to said catalyst carrier, and which consists of at least one element of the lanthanides, actinides,and the IIIb group of the periodic table of chemical elements;
d) at least one source of shortwave light of wavelengths from 250 to 400 nm, as a photon source;
e) at least one washing zone for said catalyst carrier in accordance with a), on which catalysts are applied in accordance with b) and c), through which said catalyst carrier is transported and treated with polar solvents
2. Method of claim 1, wherein said catalyst carrier consists of roughened wovens or nonwovens made of stainless steel, titanium, tantalum, niobium, zirconium, hafnium, or metals of the VIII group of the periodic table of chemical elements, whereby roughening is conducted mechanically or oxidatively, in the latter case resulting in a roughening thin oxide layer, and whereby said wovens or nonwovens are joined into packets and framed by noncorroding materials.
3. Method of claim 1, wherein said catalyst carrier consists of noncorroding, porous material.
4. Method of claim 1, wherein said catalyst carrier consists of carbon fibers or porous carbon material with a high specific surface.
5. Method of claim 1, wherein said catalyst carrier consists of ceramic material with zeolite structure.
6. Method of claim 1, wherein said catalyst carrier consists of noncorroding closed-cell organic or inorganic polymeric or polycondensation material.
7. Method of claim 1, wherein said semiconductor oxide is titanium dioxide and said precious metal is palladium or plating, used in particle form with a high specific surface.
8. Method of claim 1, wherein said semiconductor oxide is hafnium oxide or zirconium oxide and said precious metal is platinum or palladium, used in the modified form with a high specific surface.
9. Method of claim 1, wherein said elements according to c) are used as chloride salts and are, after their conversion, applied as oxides.
10. Method of claims 1 to 9, wherein a low-pressure quartz lamp is used as said light source.
11. Method of claims 1 to 10, wherein said washing zone according to e) is passed through continuously or at time intervals, resulting in a complete wetting and washing of said catalyst carrier according to a) with said catalysts according to b) and c) per time interval.
12. Method of claims 1 to 11, wherein said washing is conducted with water.
13. Method of claims 1 to 12, wherein oxidizing chemicals are added to said aqueous solution.
14. Method for photocatalytic mineralization according to claim 1, wherein mineralization of undesirable chemical substances is improved by adding mineralization aids to said substrate to be purified.
15. Method of claim 14, wherein ammonia is added to said substrate to be purified.
16. Method of claim 1, wherein at least one element according to c) is applied in an amount equaling 0 to 15 weight percent of the total amount of catalyst used.
17. Method of one or more of claims 1 to 16, wherein said substrates to be purified are fed through a fluidized bed in a physically closed system consisting of:
subitems a), b), c), and d).
subitems a), b), c), and d).
18. Method of claim 17, wherein gaseous products are produced which do not undergo a washing-out method in the system.
19. Method of claim 1, wherein said oxides according to b) have the following formulae:
M2Ox and N1M2Ox, where Ml - elements of the Ia, IIa and IIb group of the periodic table M2 - Ti, Zr, Hf, V, Nb, Ta, and elements of group IIIb, e. g., yttrium and scandium, x - an stechiometric or understechiometric value in relation to value of the Ml and M2 elements, and wherein the platinum series consists primarily of palladium, platinum, rhodium, and ruthenium.
M2Ox and N1M2Ox, where Ml - elements of the Ia, IIa and IIb group of the periodic table M2 - Ti, Zr, Hf, V, Nb, Ta, and elements of group IIIb, e. g., yttrium and scandium, x - an stechiometric or understechiometric value in relation to value of the Ml and M2 elements, and wherein the platinum series consists primarily of palladium, platinum, rhodium, and ruthenium.
20. Apparatus for carrying out the methods of one or more of claims 1 to 19, consisting of the following principal components:
f) a closed housing consisting of corrosion-resistant material equipped with inlet and outlet nozzles for said substrate and bearings and clamps for said catalyst carriers with catalysts and said sources of shortwave light;
g) a frame to hold said catalyst carrier with said catalysts;
h) an apparatus for moving said catalyst carrier and catalysts in said housing according to f);
and i) at least one source of shortwave light of wavelengths between 250 and 400 nm.
f) a closed housing consisting of corrosion-resistant material equipped with inlet and outlet nozzles for said substrate and bearings and clamps for said catalyst carriers with catalysts and said sources of shortwave light;
g) a frame to hold said catalyst carrier with said catalysts;
h) an apparatus for moving said catalyst carrier and catalysts in said housing according to f);
and i) at least one source of shortwave light of wavelengths between 250 and 400 nm.
21. Apparatus of claim 20, wherein said housing according to f) contains a cavity for receiving a bathing liquid equipped with necessary inlet and outlet nozzles for said bathing 17 quid.
22. Apparatus of claim 20, wherein said frame with said catalyst carrier and catalysts according to g) is flexibly affixed within said housing according to f) in such a way that its entirety passes through said bath according to e).
23. Apparatus of claims 20 and 21, wherein said housing according to f) contains a spraying apparatus for washing said catalyst carrier and catalysts, whereby said washing liquid returns into said bath and is recirculated for spraying.
24. Apparatus of claim 23, wherein said spraying apparatus is equipped with a time switch for interval washing.
25. Apparatus of claim 20, wherein said frame according to g) is a cylindrical body with a central axle, a cavity surrounding said axle, followed by a round container, which may be subdivided into pockets and which is connected to said axle on both sides, resulting in a closed container (14) whose outer (62) and inner (63) cylinder casings are constructed in such a manner that they are easily permeable for gases and can easily contain and fix said catalyst carriers and catalysts.
26. Apparatus of claims 20 and 21, wherein said frame according to g) is a square object in a packet which contains said catalyst carrier and catalyst and which travels up and down on vertical plain bearings within said housing according to g) and submerges in said washing liquid.
27. Apparatus of claims 20, 21, and 26, wherein two or more units are employed and switching of the feed method is synchronized in such a manner that said method is not interrupted during catalyst washing.
28. Apparatus of claim 20, wherein said frame according to g) consists of a plate which is permeable for gases when using said fluidized catalyst process for gaseous mineralization products.
29. Apparatus of claim 20, consisting of several subchambers for said substrate reaction in multi-stage processes.
30. Apparatus of claims 20 to 29, corresponding to those shown in Figs. 1 to 7.
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE4142520 | 1991-12-21 | ||
DE4241451A DE4241451A1 (en) | 1991-12-21 | 1992-12-09 | Methods and devices for cleaning gases, exhaust gases, vapors and brines from undesirable chemical substances |
DEP4241451.2 | 1992-12-09 | ||
DEP4142520.0 | 1992-12-21 |
Publications (1)
Publication Number | Publication Date |
---|---|
CA2085758A1 true CA2085758A1 (en) | 1993-06-22 |
Family
ID=25910422
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CA002085758A Abandoned CA2085758A1 (en) | 1991-12-21 | 1992-12-18 | Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brines |
Country Status (9)
Country | Link |
---|---|
EP (1) | EP0590202B1 (en) |
JP (1) | JPH05337337A (en) |
CN (1) | CN1076139A (en) |
AT (1) | ATE142898T1 (en) |
AU (1) | AU657020B2 (en) |
CA (1) | CA2085758A1 (en) |
DE (2) | DE4241451A1 (en) |
ES (1) | ES2096013T3 (en) |
MY (1) | MY109975A (en) |
Cited By (3)
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EP0738539A1 (en) * | 1993-01-18 | 1996-10-23 | PCP-PHOTOCATALYTIC PURIFICATION GmbH | Process for cleaning gases, waste gases, vapours and water containing unwanted chemical compounds |
CN113663626A (en) * | 2021-08-30 | 2021-11-19 | 江西科技学院 | Photocatalytic degradation device for copper slag waste material and use method |
CN114288971A (en) * | 2021-12-30 | 2022-04-08 | 贵州融晟环保科技有限公司 | Be used for high-efficient separator of industrial waste material valuable metal |
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ES2186733T3 (en) * | 1994-11-16 | 2003-05-16 | Toto Ltd | FUNCTIONAL PHOTOCATALITICAL MATERIAL AND METHOD TO PRODUCE IT. |
WO1996038212A2 (en) * | 1995-05-23 | 1996-12-05 | United Technologies Corp | Back-side illuminated organic pollutant removal system |
DE69735209T2 (en) * | 1996-09-20 | 2006-09-21 | Daiken Chemical Co. Ltd., Osaka | PHOTOCATALYZER WITH ULTRA-FINE METAL PARTICLES, HIGH-FUNCTIONAL MATERIAL CHARGED WITH THE PHOTO CATALYST AND METHOD FOR THEIR PRODUCTION |
NL1004961C2 (en) * | 1997-01-09 | 1998-07-13 | Dsm Nv | Monolith reactor. |
IL121877A (en) * | 1997-10-01 | 2001-09-13 | Yissum Res Dev Co | Photocatalysts for the degradation of organic pollutants |
CN1057477C (en) * | 1998-05-08 | 2000-10-18 | 湖北省化学研究所 | Steam purifying method and apparatus for change-over system of synthetic ammonia plant |
CN1112229C (en) * | 1998-05-15 | 2003-06-25 | 中国科学院成都有机化学研究所 | Method and device for treating organic pollution gas |
FR2794033B1 (en) * | 1999-05-27 | 2001-06-29 | Ahlstrom Paper Group Res And C | PROCESS FOR THE PURIFICATION OF GASEOUS EFFLUENTS BY PHOTOCATALYSIS, INSTALLATION FOR CARRYING OUT SAID METHOD |
DE10064317A1 (en) * | 2000-12-22 | 2002-10-17 | Studiengesellschaft Kohle Mbh | New photocatalysts and methods for their discovery |
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JP5822307B2 (en) * | 2012-11-22 | 2015-11-24 | 有限会社マロニエ技術研究所 | Humidifier and humidification method |
DE202013105277U1 (en) * | 2013-11-21 | 2015-03-10 | Rgenau Industries Kg | Catalyst support body |
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DE102016209952A1 (en) * | 2016-06-07 | 2017-12-07 | Robert Bosch Gmbh | filter means |
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WO2023122693A1 (en) * | 2021-12-21 | 2023-06-29 | Nitto Denko Corporation | Deactivation resistant catalytic materials and method for making the same |
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US4892712A (en) * | 1987-09-04 | 1990-01-09 | Nutech Energy Systems Inc. | Fluid purification |
JP2691751B2 (en) * | 1988-10-14 | 1997-12-17 | 株式会社日立製作所 | Catalytic structure and method and apparatus for producing the same |
JPH02169040A (en) * | 1988-12-22 | 1990-06-29 | Matsushita Electric Ind Co Ltd | Method for regenerating photocatalyst |
JP2564421B2 (en) * | 1989-08-24 | 1996-12-18 | 工業技術院長 | Ventilation equipment for road tunnels |
US5045288A (en) * | 1989-09-15 | 1991-09-03 | Arizona Board Of Regents, A Body Corporate Acting On Behalf Of Arizona State University | Gas-solid photocatalytic oxidation of environmental pollutants |
WO1991009823A1 (en) * | 1990-01-04 | 1991-07-11 | Trustees Of Boston University | Photocatalytic process for degradation of organic materials in a vaporized or gaseous state |
DE4023995C2 (en) * | 1990-07-28 | 1994-06-09 | Pcp Photocatalytic Purificatio | Method and device for fresh air and indoor air purification in motor vehicles |
-
1992
- 1992-12-09 DE DE4241451A patent/DE4241451A1/en not_active Withdrawn
- 1992-12-16 ES ES92121367T patent/ES2096013T3/en not_active Expired - Lifetime
- 1992-12-16 DE DE59207201T patent/DE59207201D1/en not_active Expired - Fee Related
- 1992-12-16 EP EP92121367A patent/EP0590202B1/en not_active Expired - Lifetime
- 1992-12-16 AT AT92121367T patent/ATE142898T1/en not_active IP Right Cessation
- 1992-12-18 CA CA002085758A patent/CA2085758A1/en not_active Abandoned
- 1992-12-21 MY MYPI92002356A patent/MY109975A/en unknown
- 1992-12-21 CN CN92115370A patent/CN1076139A/en active Pending
- 1992-12-21 JP JP4361827A patent/JPH05337337A/en active Pending
- 1992-12-21 AU AU30341/92A patent/AU657020B2/en not_active Ceased
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0738539A1 (en) * | 1993-01-18 | 1996-10-23 | PCP-PHOTOCATALYTIC PURIFICATION GmbH | Process for cleaning gases, waste gases, vapours and water containing unwanted chemical compounds |
CN113663626A (en) * | 2021-08-30 | 2021-11-19 | 江西科技学院 | Photocatalytic degradation device for copper slag waste material and use method |
CN113663626B (en) * | 2021-08-30 | 2022-09-20 | 江西科技学院 | Photocatalytic degradation device for copper slag waste material and use method |
CN114288971A (en) * | 2021-12-30 | 2022-04-08 | 贵州融晟环保科技有限公司 | Be used for high-efficient separator of industrial waste material valuable metal |
Also Published As
Publication number | Publication date |
---|---|
ES2096013T3 (en) | 1997-03-01 |
EP0590202B1 (en) | 1996-09-18 |
ATE142898T1 (en) | 1996-10-15 |
MY109975A (en) | 1997-10-31 |
JPH05337337A (en) | 1993-12-21 |
CN1076139A (en) | 1993-09-15 |
DE59207201D1 (en) | 1996-10-24 |
AU657020B2 (en) | 1995-02-23 |
EP0590202A1 (en) | 1994-04-06 |
AU3034192A (en) | 1993-06-24 |
DE4241451A1 (en) | 1993-12-16 |
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