CN110116007A - A kind of wastewater from chemical industry catalytic ozonation catalysts for treating and preparation method - Google Patents
A kind of wastewater from chemical industry catalytic ozonation catalysts for treating and preparation method Download PDFInfo
- Publication number
- CN110116007A CN110116007A CN201810118624.1A CN201810118624A CN110116007A CN 110116007 A CN110116007 A CN 110116007A CN 201810118624 A CN201810118624 A CN 201810118624A CN 110116007 A CN110116007 A CN 110116007A
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- Prior art keywords
- oxide
- carrier
- catalyst
- quality
- maceration extract
- Prior art date
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- 239000003054 catalyst Substances 0.000 title claims abstract description 148
- 239000002351 wastewater Substances 0.000 title claims abstract description 54
- 238000002360 preparation method Methods 0.000 title claims abstract description 35
- 230000003197 catalytic effect Effects 0.000 title claims abstract description 33
- 239000000126 substance Substances 0.000 title claims abstract description 30
- 238000006385 ozonation reaction Methods 0.000 title claims abstract description 17
- 229910000420 cerium oxide Inorganic materials 0.000 claims abstract description 67
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 claims abstract description 67
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims abstract description 58
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims abstract description 47
- 239000010949 copper Substances 0.000 claims abstract description 26
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims abstract description 24
- 229910052802 copper Inorganic materials 0.000 claims abstract description 24
- 229910052742 iron Inorganic materials 0.000 claims abstract description 23
- 238000012545 processing Methods 0.000 claims abstract description 23
- 229910052759 nickel Inorganic materials 0.000 claims abstract description 21
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims abstract description 16
- 238000002803 maceration Methods 0.000 claims description 136
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 claims description 130
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 74
- 238000000034 method Methods 0.000 claims description 49
- -1 haydite Chemical compound 0.000 claims description 48
- GNRSAWUEBMWBQH-UHFFFAOYSA-N oxonickel Chemical compound [Ni]=O GNRSAWUEBMWBQH-UHFFFAOYSA-N 0.000 claims description 43
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical group [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 claims description 42
- 229910000480 nickel oxide Inorganic materials 0.000 claims description 41
- 230000008569 process Effects 0.000 claims description 41
- 238000005470 impregnation Methods 0.000 claims description 36
- 238000001354 calcination Methods 0.000 claims description 35
- 239000002243 precursor Substances 0.000 claims description 34
- 238000010521 absorption reaction Methods 0.000 claims description 24
- 238000007254 oxidation reaction Methods 0.000 claims description 23
- 239000008367 deionised water Substances 0.000 claims description 22
- 229910044991 metal oxide Inorganic materials 0.000 claims description 21
- 150000004706 metal oxides Chemical class 0.000 claims description 21
- 230000003647 oxidation Effects 0.000 claims description 20
- 229910052684 Cerium Inorganic materials 0.000 claims description 19
- 229910052751 metal Inorganic materials 0.000 claims description 18
- 239000002184 metal Substances 0.000 claims description 18
- 229910021641 deionized water Inorganic materials 0.000 claims description 12
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 claims description 11
- 230000000694 effects Effects 0.000 claims description 10
- 238000005303 weighing Methods 0.000 claims description 9
- 150000001875 compounds Chemical class 0.000 claims description 8
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 claims description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 6
- 238000004090 dissolution Methods 0.000 claims description 6
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 claims description 6
- 229910052737 gold Inorganic materials 0.000 claims description 6
- 239000010931 gold Substances 0.000 claims description 6
- 229910052760 oxygen Inorganic materials 0.000 claims description 6
- 239000001301 oxygen Substances 0.000 claims description 6
- 238000001035 drying Methods 0.000 claims description 5
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 claims description 5
- 239000004411 aluminium Substances 0.000 claims description 4
- 229910052782 aluminium Inorganic materials 0.000 claims description 4
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 4
- 230000008859 change Effects 0.000 claims description 4
- 239000002808 molecular sieve Substances 0.000 claims description 4
- RVTZCBVAJQQJTK-UHFFFAOYSA-N oxygen(2-);zirconium(4+) Chemical compound [O-2].[O-2].[Zr+4] RVTZCBVAJQQJTK-UHFFFAOYSA-N 0.000 claims description 4
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims description 4
- 229910001928 zirconium oxide Inorganic materials 0.000 claims description 4
- 239000003795 chemical substances by application Substances 0.000 claims description 3
- QTBSBXVTEAMEQO-UHFFFAOYSA-M Acetate Chemical compound CC([O-])=O QTBSBXVTEAMEQO-UHFFFAOYSA-M 0.000 claims description 2
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 claims description 2
- 150000004675 formic acid derivatives Chemical class 0.000 claims description 2
- ZMIGMASIKSOYAM-UHFFFAOYSA-N cerium Chemical compound [Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce] ZMIGMASIKSOYAM-UHFFFAOYSA-N 0.000 claims 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical class O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims 1
- 238000006555 catalytic reaction Methods 0.000 claims 1
- 239000000470 constituent Substances 0.000 claims 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 claims 1
- 239000000460 chlorine Substances 0.000 abstract description 23
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 abstract description 21
- 229910052801 chlorine Inorganic materials 0.000 abstract description 21
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 abstract description 12
- 239000010865 sewage Substances 0.000 abstract description 4
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 74
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 31
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 23
- 239000005751 Copper oxide Substances 0.000 description 22
- 229910000431 copper oxide Inorganic materials 0.000 description 22
- VCJMYUPGQJHHFU-UHFFFAOYSA-N iron(3+);trinitrate Chemical group [Fe+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VCJMYUPGQJHHFU-UHFFFAOYSA-N 0.000 description 20
- 229910003158 γ-Al2O3 Inorganic materials 0.000 description 20
- GWXLDORMOJMVQZ-UHFFFAOYSA-N cerium Chemical compound [Ce] GWXLDORMOJMVQZ-UHFFFAOYSA-N 0.000 description 17
- 238000010438 heat treatment Methods 0.000 description 15
- 239000007787 solid Substances 0.000 description 14
- 238000001179 sorption measurement Methods 0.000 description 14
- 238000007598 dipping method Methods 0.000 description 13
- 238000003756 stirring Methods 0.000 description 13
- 238000010792 warming Methods 0.000 description 13
- 239000004744 fabric Substances 0.000 description 12
- 238000006243 chemical reaction Methods 0.000 description 11
- XTVVROIMIGLXTD-UHFFFAOYSA-N copper(II) nitrate Chemical compound [Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XTVVROIMIGLXTD-UHFFFAOYSA-N 0.000 description 10
- HSJPMRKMPBAUAU-UHFFFAOYSA-N cerium(3+);trinitrate Chemical compound [Ce+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O HSJPMRKMPBAUAU-UHFFFAOYSA-N 0.000 description 9
- 230000006835 compression Effects 0.000 description 9
- 238000007906 compression Methods 0.000 description 9
- SXTLQDJHRPXDSB-UHFFFAOYSA-N copper;dinitrate;trihydrate Chemical compound O.O.O.[Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O SXTLQDJHRPXDSB-UHFFFAOYSA-N 0.000 description 9
- 229910052593 corundum Inorganic materials 0.000 description 9
- 150000002823 nitrates Chemical class 0.000 description 9
- 229910001845 yogo sapphire Inorganic materials 0.000 description 9
- QQZMWMKOWKGPQY-UHFFFAOYSA-N cerium(3+);trinitrate;hexahydrate Chemical compound O.O.O.O.O.O.[Ce+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O QQZMWMKOWKGPQY-UHFFFAOYSA-N 0.000 description 8
- UOGMEBQRZBEZQT-UHFFFAOYSA-L manganese(2+);diacetate Chemical compound [Mn+2].CC([O-])=O.CC([O-])=O UOGMEBQRZBEZQT-UHFFFAOYSA-L 0.000 description 8
- MQRWBMAEBQOWAF-UHFFFAOYSA-N acetic acid;nickel Chemical compound [Ni].CC(O)=O.CC(O)=O MQRWBMAEBQOWAF-UHFFFAOYSA-N 0.000 description 7
- 229940071125 manganese acetate Drugs 0.000 description 7
- MIVBAHRSNUNMPP-UHFFFAOYSA-N manganese(2+);dinitrate Chemical compound [Mn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MIVBAHRSNUNMPP-UHFFFAOYSA-N 0.000 description 7
- 239000011259 mixed solution Substances 0.000 description 7
- 229940078494 nickel acetate Drugs 0.000 description 7
- SPIFDSWFDKNERT-UHFFFAOYSA-N nickel;hydrate Chemical compound O.[Ni] SPIFDSWFDKNERT-UHFFFAOYSA-N 0.000 description 7
- 239000007921 spray Substances 0.000 description 7
- BZDIAFGKSAYYFC-UHFFFAOYSA-N manganese;hydrate Chemical compound O.[Mn] BZDIAFGKSAYYFC-UHFFFAOYSA-N 0.000 description 6
- 238000005259 measurement Methods 0.000 description 6
- 150000003839 salts Chemical class 0.000 description 6
- OANFWJQPUHQWDL-UHFFFAOYSA-N copper iron manganese nickel Chemical compound [Mn].[Fe].[Ni].[Cu] OANFWJQPUHQWDL-UHFFFAOYSA-N 0.000 description 5
- 239000007788 liquid Substances 0.000 description 5
- KBJMLQFLOWQJNF-UHFFFAOYSA-N nickel(ii) nitrate Chemical compound [Ni+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O KBJMLQFLOWQJNF-UHFFFAOYSA-N 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 4
- OPQARKPSCNTWTJ-UHFFFAOYSA-L copper(ii) acetate Chemical compound [Cu+2].CC([O-])=O.CC([O-])=O OPQARKPSCNTWTJ-UHFFFAOYSA-L 0.000 description 4
- 238000002156 mixing Methods 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 238000012360 testing method Methods 0.000 description 4
- XMOKRCSXICGIDD-UHFFFAOYSA-N acetic acid;nickel Chemical compound [Ni].CC(O)=O XMOKRCSXICGIDD-UHFFFAOYSA-N 0.000 description 3
- 230000008901 benefit Effects 0.000 description 3
- VGBWDOLBWVJTRZ-UHFFFAOYSA-K cerium(3+);triacetate Chemical compound [Ce+3].CC([O-])=O.CC([O-])=O.CC([O-])=O VGBWDOLBWVJTRZ-UHFFFAOYSA-K 0.000 description 3
- 238000001223 reverse osmosis Methods 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- 229910002651 NO3 Inorganic materials 0.000 description 2
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- OXBLHERUFWYNTN-UHFFFAOYSA-M copper(I) chloride Chemical compound [Cu]Cl OXBLHERUFWYNTN-UHFFFAOYSA-M 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 229910052594 sapphire Inorganic materials 0.000 description 2
- 229910006415 θ-Al2O3 Inorganic materials 0.000 description 2
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical compound [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 description 1
- WAEMQWOKJMHJLA-UHFFFAOYSA-N Manganese(2+) Chemical compound [Mn+2] WAEMQWOKJMHJLA-UHFFFAOYSA-N 0.000 description 1
- VEQPNABPJHWNSG-UHFFFAOYSA-N Nickel(2+) Chemical compound [Ni+2] VEQPNABPJHWNSG-UHFFFAOYSA-N 0.000 description 1
- DQMUQFUTDWISTM-UHFFFAOYSA-N O.[O-2].[Fe+2].[Fe+2].[O-2] Chemical compound O.[O-2].[Fe+2].[Fe+2].[O-2] DQMUQFUTDWISTM-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 1
- URDFSSZCFPLLKR-UHFFFAOYSA-N [Ce].[Mn].[Ni].[Cu] Chemical compound [Ce].[Mn].[Ni].[Cu] URDFSSZCFPLLKR-UHFFFAOYSA-N 0.000 description 1
- BQCFCWXSRCETDO-UHFFFAOYSA-N [Fe].[Mn].[Cu] Chemical compound [Fe].[Mn].[Cu] BQCFCWXSRCETDO-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- XQTIWNLDFPPCIU-UHFFFAOYSA-N cerium(3+) Chemical class [Ce+3] XQTIWNLDFPPCIU-UHFFFAOYSA-N 0.000 description 1
- DRVWBEJJZZTIGJ-UHFFFAOYSA-N cerium(3+);oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[Ce+3].[Ce+3] DRVWBEJJZZTIGJ-UHFFFAOYSA-N 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000000306 component Substances 0.000 description 1
- GOECOOJIPSGIIV-UHFFFAOYSA-N copper iron nickel Chemical compound [Fe].[Ni].[Cu] GOECOOJIPSGIIV-UHFFFAOYSA-N 0.000 description 1
- UTICYDQJEHVLJZ-UHFFFAOYSA-N copper manganese nickel Chemical compound [Mn].[Ni].[Cu] UTICYDQJEHVLJZ-UHFFFAOYSA-N 0.000 description 1
- HFDWIMBEIXDNQS-UHFFFAOYSA-L copper;diformate Chemical compound [Cu+2].[O-]C=O.[O-]C=O HFDWIMBEIXDNQS-UHFFFAOYSA-L 0.000 description 1
- ODDZENUCCGSDGC-UHFFFAOYSA-N copper;n'-[2-[2-(2-aminoethylamino)ethylamino]ethyl]ethane-1,2-diamine;gold(1+);tetracyanide Chemical compound [Cu+2].[Au+].[Au+].N#[C-].N#[C-].N#[C-].N#[C-].NCCNCCNCCNCCN ODDZENUCCGSDGC-UHFFFAOYSA-N 0.000 description 1
- 238000012937 correction Methods 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 235000000396 iron Nutrition 0.000 description 1
- SZVJSHCCFOBDDC-UHFFFAOYSA-N iron(II,III) oxide Inorganic materials O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 description 1
- 230000005923 long-lasting effect Effects 0.000 description 1
- 150000002696 manganese Chemical class 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- 150000004965 peroxy acids Chemical class 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 239000010936 titanium Substances 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N titanium dioxide Inorganic materials O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/002—Mixed oxides other than spinels, e.g. perovskite
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/76—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/84—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/889—Manganese, technetium or rhenium
- B01J23/8892—Manganese
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/0201—Impregnation
- B01J37/0213—Preparation of the impregnating solution
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2523/00—Constitutive chemical elements of heterogeneous catalysts
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/12—Halogens or halogen-containing compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
- C02F2305/023—Reactive oxygen species, singlet oxygen, OH radical
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Materials Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Catalysts (AREA)
Abstract
The invention discloses a kind of wastewater from chemical industry catalytic ozonation catalysts for treating and preparation method, which includes carrier and active component, and wherein active component is metallic copper, iron, nickel, manganese, cerium oxide.Catalyst of the invention is high to TDS content, and the catalytic ozonation processing of the high high salinity and chlorine wastewater from chemical industry of chloride ion content has good catalytic activity, and wastewater COD removal rate reaches 40% or more.Catalyst of the invention is suitable for the advanced treating of bio-chemical effluent of the sewage treatment plant containing high salinity and chlorine.
Description
Technical field
The present invention relates to catalyst of a kind of advanced treatment of industrial waste water and preparation method thereof, in particular to a kind of Industry Waste
The catalyst and preparation method thereof of water-ozone catalytic oxidation treatment, belongs to water process and catalytic field.
Background of invention
High salinity and chlorine wastewater from chemical industry refers to that the total dissolved solid content of chemical enterprise emission is higher than 5000mg/L, chloride ion
Content is higher than 2000mg/L, the waste water containing hardly degraded organic substance.The total dissolubility of the bio-chemical effluent of certain Craft in Chemical Industrial Area sewage treatment plant is solid
Body (TDS) content about 12000mg/L, chloride ion content about 6000mg/L, COD value meet height with high salt between 80~120mg/L
The feature of chloride wastewater.Reverse osmosis technology is widely applied in engineering fields such as coal chemical industry wastewater zero emissions.Part reverse osmosis concentrated water
Feature with high salinity and chlorine waste water.Because COD value of waste water is higher than the level-one A of " urban wastewater treatment firm pollutant emission standard "
Standard, such waste water need advanced treating.Catalytic ozonation method is one for the treatment of process of industrial application.It is with technique letter
Advantage single, reaction is mild, without secondary pollution.
Chloride ion, sulfate ion etc. have inhibition to make the active group hydroxyl radical free radical generated in catalytic ozonation
With, many catalyst of good performance in less salt waste water by ozone oxidation process are often lower to the activity of high salinity and chlorine waste water,
Stability is insufficient.It develops and is suitble to the ozone catalytic oxidation catalyst of high salinity and chlorine Sewage advanced treatment particularly important.
Mehdi Ahmadi has reported a kind of activated carbon supported Fe3O4Catalyst (Separation and
Purification Technology, 2017,177:293-303).The catalyst is to total dissolved solid content 37000mg/
L, the petrochemical wastewater of COD value 360mg/L has greater activity.However exists using active carbon as the mechanical strength of the catalyst of carrier and lack
It falls into, will appear damaged loss in operation.
For a long time in ozone oxidation environment after use, the surface chemical property of active carbon can change, catalytic activity by
It gradually reduces, needs regular regeneration (Chinese water supply and drainage, 2010,26 (4): 6-9,14).
Patent 201510508937.4 discloses a kind of halophilic ozone catalytic oxidation catalyst.By CuO, TiO2Load
In the activated alumina ball of 2-4mm.The catalyst is evaluated under dynamic continuous flow operational mode, ozone dosage 100mg/L,
Wastewater volume air speed 1h-1, waste water TDS about 3500mg/L, COD about 350mg/L.Measuring wastewater COD removal rate is 31%.Water outlet
COD233mg/L is higher than discharge level-one A standard.The catalyst can only be useless no more than 8000mg/L in total dissolved solid content
Normal use in water.
Patent 201610067240.2 discloses a kind of ozone catalytic oxidation catalyst for handling reverse osmosis concentrated water.With dipping
The nitrate such as titanium, manganese, iron, potassium are supported on the alumina support through peracid or alkali process by method, are made through health, drying, roasting
Obtain catalyst.Test condition is that the mass concentration of waste water chloride ion is 2500mg/L, COD200mg/L.Wastewater volume air speed 2h
-1, ozone usage 860mg/L, wastewater COD removal rate 60%, water outlet COD, which is still higher than, discharges level-one A standard.Ozone dosage is big,
It is economically uneconomical.
Summary of the invention
The purpose of the present invention is deposit in the catalytic ozonation treatment process for existing degradation high salinity and chlorine wastewater from chemical industry
The technical issues of, a kind of high salinity and chlorine wastewater from chemical industry catalytic ozonation catalysts for treating and preparation method thereof is provided.This
The catalyst of invention is high to the COD removal efficiency of high salinity and chlorine chemical industrial organic wastewater;Stability is high;Compression strength is high.Catalyst
Preparation method simple process, can accurately control the load capacity of active component, and active component is uniformly dispersed, in preparation process
No waste residue, waste water generate, preparation process low pollution.
Three kinds of reaction paths are existed simultaneously in ozone heterogeneous catalytic oxidation reaction system.1, the ozone of water phase ontology is direct
Oxidation reaction;2, the HO indirect oxidation reaction of water phase ontology;3, the ozone of the organic species of catalyst surface absorption and absorption
Between reaction.When water phase ontology contains the Cl of high concentration-When, such as reaction equation (1), chloride ion consumes hydroxyl radical free radical,
The reaction of HO indirect oxidation is suppressed, thus the third reaction just seems more important.The group that the present invention passes through regulation catalyst
At and preparation method, the surface texture of catalyst obtained be conducive to adsorb waste water in solubilised state organic matter and ozone, strengthen
The reaction of the third approach realizes qualified discharge to remove the COD of waste water with less ozone usage.
HO·+Cl-→Cl·+OH- (1)
To achieve the purpose of the present invention, one aspect of the present invention provides a kind of processing of wastewater from chemical industry catalytic ozonation with urging
Agent, including catalyst carrier and catalytic active component, wherein the active component is the oxidation of metallic copper, iron, nickel, manganese, cerium
Object.
Wherein, the wastewater from chemical industry is high salinity and chlorine organic wastewater.
In particular, the high salinity and chlorine organic wastewater refers in water that TDS content is≤15000mg/L, preferably 2000~
15000mg/L;Chloride ion content >=1000mg/L, preferably 1000~6000mg/L;COD >=70mg/L, preferably 70~
The waste water of 120mg/L.
In particular, the catalyst is that high salinity and chlorine wastewater from chemical industry carries out catalytic ozonation catalysts for treating.
Wherein, the carrier selective oxidation aluminium, molecular sieve, haydite, zirconium oxide, preferably aluminium oxide and haydite, it is further excellent
It is selected as aluminium oxide.
In particular, the aluminium oxide can be γ-Al2O3、α-Al2O3、δ-Al2O3、η-Al2O3、θ-Al2O3, preferably brilliant
Type is γ-Al2O3。
Especially, the γ-Al2O3Carrier specific surface area be 150~400m2/ g, preferably 220~320m2/g.Carrier
0.2~0.5cm of Kong Rongwei3/ g, preferably 0.38~0.43cm3/g;Carrier compression strength >=130N/.
Especially, the support shapes can be spherical, bar shaped, cylinder, trilobal, honeycomb etc., preferably spherical,
Bar shaped, it is further preferably spherical.
In particular, the diameter of the ball type carrier is 2~8mm, preferably 3~5mm.
Because the aperture of catalyst, in 2 times of target molecule diameters, the absorption property of catalyst is best, while industrial application
It has higher requirements to the mechanical strength of catalyst, the γ-Al that the present invention uses2O3Preferably specific standard, i.e. specific surface area 220-
320m2/ g, Kong Rong 0.38-0.43cm3/ g, compression strength are greater than the spherical gamma-Al of 130N/, partial size 3-5mm2O3。
Wherein, metallic copper in the active component, iron, nickel, manganese, cerium oxide be respectively CuO, Fe2O3、NiO、MnO2、
CeO2。
In particular, the weight of the activity component metal Cu oxide and catalyst is (0.1-1.5): 100, it is excellent
It is selected as (0.5-1.5): 100, further preferably (0.5-1.0): 100;The weight of metal ferriferous oxide and catalyst
For (0.1-1.5): 100, preferably (0.25-1.1): 100, further preferably (0.25-0.9): 100;Metal nickel oxide
Weight with catalyst is (0.1-1.5): 100, preferably (0.3-1.0): 100;Metal manganese oxide and catalyst
Weight be (0.5-3): 100, preferably (1.5-3.0): 100;The parts by weight of metallic cerium oxide and catalyst are matched
Than for (0.05-0.7): 100, preferably (0.2-0.7): 100, further preferably (0.2-0.5): 100.
Especially, the weight of the metallic copper, iron, nickel, manganese, the total weight parts of cerium oxide and catalyst is
(3-6): 100, preferably (3-5.5): 100, further preferably (3.8-5.5): 100, it is still more preferably (3.8-
5.05):100。
Another aspect of the present invention provides a kind of preparation method of catalytic ozonation processing wastewater from chemical industry catalyst, including
The step of following sequence carries out:
1) water absorption rate (Y, %) of carrier is measured;
2) it is weighed to calculate institute for the catalyst carrier of accurate weighing certain mass, and the water absorption rate measured according to step 1)
Catalyst carrier carries out the volume of maceration extract required when incipient impregnation processing;
3) active component precursors are added to the water dissolution, precursor maceration extract is made;Wherein, the active component precursors choosing
Select the salt compounds of metallic copper, iron, nickel, manganese, cerium;
4) active component precursors maceration extract prepared by step 3) step 2) is carried on using incipient impregnation facture to claim
In the carrier of amount;
5) carrier after impregnation is successively dried, calcination process.
Wherein, the wastewater from chemical industry is high salinity and chlorine organic wastewater.
In particular, the high salinity and chlorine organic wastewater refers in water that TDS content is≤15000mg/L, preferably 2000~
15000mg/L;Chloride ion content >=1000mg/L, preferably 1000~6000mg/L;COD >=70mg/L, preferably 70~
The waste water of 120mg/L.
Wherein, the aluminium of carrier selective oxidation described in step 1), molecular sieve, haydite, zirconium oxide, preferably aluminium oxide and haydite,
Further preferably aluminium oxide.
In particular, the aluminium oxide can be γ-Al2O3、α-Al2O3、δ-Al2O3、η-Al2O3、θ-Al2O3, preferably brilliant
Type is γ-Al2O3。
Especially, the crystal form is γ-Al2O3Carrier be spherical shape.
Wherein, the water absorption rate of catalyst carrier is measured in step 1) in accordance with the following steps, accurately weighs sample 50g (m, essence
Really to 0.01g);It is put into beaker, adds water to submerge, constantly stir, separated water with sample with funnel after 1h, place 10min, then
Weigh sample quality (m after absorbing water1, it is accurate to 0.01g);The water absorption rate (Y, %) of carrier is calculated according to formula (1),
Y=(m1-m)/m×100 (1)
Wherein, m1 is the quality (g) of carrier after water suction, and m is the quality (g) of carrier.
In particular, the water absorption rate is the quality (g) for the moisture that every 100g catalyst carrier absorbs.
Usually by weight of the volume of every 1g water carries out for 1ml, therefore the water absorption rate is the suction of every 100g catalyst carrier
The volume (ml) of the moisture of receipts.
For example, accurately weighing the quality (M, g) of catalyst carrier, then when carrying out incipient impregnation processing, institute in step 2)
The volume of the maceration extract needed is (M × Y/100, ml).
Wherein, the salt compounds of metal described in step 3) are nitrate, acetate or formates.
Especially, active component precursors select metallic copper (2+), iron (3+), nickel (2+), manganese (2+), cerium (3+) salt chemical combination
Object.
In particular, the salt compounds of the metallic copper are copper nitrate or copper acetate or copper formate;The salt of metallic iron
Conjunction object is ferric nitrate;The salt compounds of metallic nickel are nickel nitrate or nickel acetate;The salt compounds of manganese metal are 50% (w/w)
Manganese nitrate aqueous solution or manganese acetate;The salt compounds cerous nitrate or cerous acetate of metallic cerium.
Wherein, the salt compounds for the active component precursors metallic copper being add to deionized water in step 3) are converted into gold
Carrier (γ-the Al that quality and step 2) after belonging to oxide (CuO) weigh2O3) and the metal oxygen that is converted into of active component precursors
Compound (CuO, Fe2O3、NiO、MnO2、CeO2) quality summation ratio be (0.1-1.5): 100, preferably (0.5-
1.5): 100, further preferably (0.5-1.0): 100;The salt compounds of metallic iron are converted into metal oxide (Fe2O3) after
Quality and step 2) weigh carrier (γ-Al2O3) and active component precursors metal oxide (CuO, Fe for being converted into2O3、
NiO、MnO2、CeO2) quality summation ratio be (0.1-1.5): 100, preferably (0.25-1.1): 100, further it is excellent
It is selected as (0.25-0.9): 100;The salt compounds of metallic nickel are converted into the quality after metal oxide (NiO) and step 2) claims
Carrier (γ-the Al of amount2O3) and active component precursors metal oxide (CuO, Fe for being converted into2O3、NiO、MnO2、CeO2) matter
The ratio of the summation of amount is (0.1-1.5): 100, preferably (0.3-1.0): 100;The salt compounds of manganese metal are converted into gold
Belong to oxide (MnO2) after quality and step 2) weigh carrier (γ-Al2O3) and the metal oxygen that is converted into of active component precursors
Compound (CuO, Fe2O3、NiO、MnO2、CeO2) quality summation ratio be (0.5-3): 100, preferably (1.5-3.0):
100;The salt compounds of metallic cerium are converted into metal oxide (CeO2) after quality and step 2) weigh carrier (γ-
Al2O3) and active component precursors metal oxide (CuO, Fe for being converted into2O3、NiO、MnO2、CeO2) quality summation ratio
Example is (0.05-0.7): 100, preferably (0.2-0.7): 100, further preferably (0.2-0.5): 100.
Such as: it is A1 that the salt compounds of active component precursors metallic copper, which are converted into the quality after metal oxide (CuO),
The salt compounds of metallic iron are converted into metal oxide (Fe2O3) after quality A2, the salt compounds of metallic nickel are converted into gold
Quality A3 after belonging to oxide (NiO), the salt compounds of manganese metal are converted into metal oxide (MnO2) after quality A4, gold
The salt compounds for belonging to cerium are converted into metal oxide (CeO2) after quality A5, step 2) weigh carrier quality be B, then
A1/ (A1+A2+A3+A4+A5+B) is (0.1-1.5): 100, preferably (0.5-1.5): 100;Other active component irons, nickel,
Manganese, proportion of oxide of cerium and so on.
Especially, the metallic copper, iron, nickel, manganese, cerium salt compounds be converted into metal oxide (CuO, Fe2O3、
NiO、MnO2、CeO2) gross mass and step 2) weigh carrier (γ-Al2O3) and the metal oxygen that is converted into of active component precursors
Compound (CuO, Fe2O3、NiO、MnO2、CeO2) quality summation ratio be (3-6): 100, preferably (3-5.5): 100,
Further preferably (3.8-5.5): 100, it is still more preferably (3.8-5.05): 100.
Wherein, weighed carrier carries out incipient impregnation in the volume and step 2) of the precursor maceration extract of step 3) preparation
The volume of required maceration extract is identical when processing.
In particular, precursor maceration extract described in step 3) is prepared in accordance with the following steps: successively by active component precursors
It is add to deionized water, stirs, then dissolution adds deionized water to the load with the weighing being calculated in step 2) again
Body carries out the volume of maceration extract required when incipient impregnation processing.
Especially, the sequence that 5 kinds of active component precursors are add to deionized water is successively are as follows: the salt of manganese metal
Close the salt of object, the salt compounds of metallic iron, the salt compounds of metallic nickel, the salt compounds of metallic cerium, metallic copper
Close object.
Manganese metal salt compound dosage is larger in the present invention, and rate of dissolution is slow in water, during preparation maceration extract first
Manganese metal salt compound is added and is conducive to being completely dissolved for 5 kinds of active component precursors compounds, is particularly due to manganese acetate in water
Rate of dissolution is lower, and dissolution manganese salt first is conducive to reach being completely dissolved for salt compounds as early as possible;If containing second in solution
And then compound nantokite is added in acid ion, will generate the lesser copper acetate of solubility, the stability of maceration extract is caused to subtract
It is weak, therefore during preparing maceration extract, it needs finally to add compound nantokite.
Wherein, incipient impregnation facture described in step 4) is that the active component precursors maceration extract for preparing step 3) sprays
On the carrier for pouring step 2) weighing;Or active component precursors maceration extract prepared by step 3) is poured into the carrier of step 2) weighing
In, so that active component precursors maceration extract is adsorbed on carrier.
In particular, static placement 3-12h is preferably quiet during impregnation after precursor maceration extract is adsorbed on carrier
Only place 6-10h.
Wherein, drying temperature described in step 5) is 100-120 DEG C;Drying time is at least 2h, preferably 2-7h.
In particular, preferably 120 DEG C of the drying temperature;It is 4 hours dry or more, preferably 4-7h.
Wherein, calcination process described in step 5) is to roast 1-2h at 300-350 DEG C, then heats to 400~550 DEG C
Roast 3-5h.
In particular, calcination process described in step 5) carries out in accordance with the following steps:
5-1) by the carrier after impregnation with the heating rate of≤10 DEG C/min from room temperature to 300-350 DEG C, and
1-2h is kept under conditions of 300-350 DEG C;
It 5-2) is warming up to 400-550 DEG C with the rate of≤10 DEG C/min again, and keeps 3- under conditions of 400-550 DEG C
5h。
In particular, step 5-1) described in heating rate be preferably 4-5 DEG C/min;Step 5-2) described in heating rate it is excellent
It is selected as 2.5-5 DEG C/min, further preferably 4-5 DEG C/min.
In particular, step 5-1) in keep 1-1.5h under conditions of 350 DEG C;Step 5-2) in preferably with 4-5 DEG C/min
Rate be warming up to 400-550 DEG C, and keep 3-5h under conditions of 400-550 DEG C.
Especially, step 5-2) in be preferably warming up to 460-500 DEG C with the rate of 4-5 DEG C/min, and at 460-500 DEG C
Under the conditions of keep 3-5h.
Another aspect of the invention provides a kind of catalytic ozonation processing wastewater from chemical industry being prepared according to the method described above
Use catalyst.
Compared with prior art, the present invention having the advantage that and effect:
1, in catalytic ozonation processing high salinity and chlorine waste water reaction, catalyst of the present invention is to organic matter in wastewater from chemical industry
Adsorption strength be greater than organic species and absorption that catalyst surface absorption is promoted to the adsorption strength of chloride ion ozone it
Between reaction, 15000mg/L is not more than to TDS content, chloride ion content goes out no more than sewage treatment plant's biochemistry of 6000mg/L
Water COD removal rate reaches 40% or more;
2, the preparation method of catalyst of the invention is simple, easy to operate, not only can accurately control the negative of active component
Carrying capacity, and active component is uniformly dispersed, and generates in preparation process without waste residue, waste water, preparation process low pollution;
3, the catalyst compression strength of catalytic ozonation of the invention is high, and the compression strength of catalyst is greater than 100N/,
Conducive to long-lasting catalytic use;
4, the preparation method of catalyst of the present invention is conducive to the content for accurately controlling active component in catalyst, obtained to urge
Agent Active components distribution is uniform, and copper oxide, di-iron trioxide, nickel monoxide, manganese dioxide, ceria play collaboration effect
It answers, improves the activity of catalyst, increase the COD removal efficiency to wastewater from chemical industry.
Specific embodiment
Present invention will be further explained below with reference to specific examples, the advantages and features of the present invention will be with description and
It is apparent.But examples are merely exemplary for these, and it is not intended to limit the scope of the present invention in any way.Those skilled in the art
Member it should be understood that without departing from the spirit and scope of the invention can details to technical solution of the present invention and form into
Row modifications or substitutions, but these modifications and replacement are fallen within the protection scope of the present invention.
Metal salt compound used in the embodiment of the present invention is purchased from Shanghai fuzz Chemical Co., Ltd.;Carrier γ-
Al2O3Particle is purchased from Zibo Ying He Chemical Co., Ltd., and carrier has the feature that
150~400m of carrier specific surface area2/ g carrier hole holds 0.38~0.43cm3/g
Compression strength >=130N/
The measurement of 1 carrier water absorption rate of embodiment
Weigh carrier γ-Al2O3Particle 50g (m is accurate to 0.01g);It is put into beaker, adds water to submerge, constantly stir, 1h
Water is separated with funnel with sample afterwards, places 10min, then weighs sample quality after water suction (m1 is accurate to 0.01g).According to public affairs
The water absorption rate (Y, %) of formula (1) calculating carrier.
Carrier γ-Al in embodiment of the present invention2O3The water absorption rate of particle is 55.0%, i.e., every 100g carrier (γ-
Al2O3) amount of moisture is fully absorbed as 55ml.
2 catalyst preparation of embodiment
1,380g carrier γ-Al is weighed2O3, spare.
It 2, is 55% according to the carrier water absorption rate Y that embodiment 1 measures, by weight of the volume of every 1g water carries out for 1ml, because
The water absorption rate of this carrier is that the volume for the moisture that every 100g catalyst carrier absorbs is 55ml, then 380g catalytic pretreatment carries
The volume that body carries out the solution of incipient impregnation weighing is 380 × 55/100=209ml.
3, maceration extract is prepared
Portions of de-ionized water is taken, 50% manganese nitrate aqueous solution (49.4g), nine water ferric nitrates (5.1g), six water are sequentially added
Nickel nitrate (4.7g), cerium nitrate hexahydrate (5.3g), nitrate trihydrate copper (12.2g) stir 30 minutes, are completely dissolved solid, then plus
Enter deionized water, until the total volume of mixed solution is 209ml, maceration extract (i.e. copper-iron-manganese-nickel-cerium salt maceration extract) be made,
Spare, wherein copper nitrate is converted into the quality of copper oxide (CuO) in maceration extract, ferric nitrate is converted into iron oxide (Fe2O3) matter
Amount, nickel nitrate is converted into the quality of nickel oxide (NiO), manganese nitrate is converted into manganese oxide (MnO2) quality, cerous nitrate is converted into
Cerium oxide (CeO2) quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, manganese oxide, the quality of cerium oxide and title
The summation of the carrier quality (380g) taken) mass ratio be respectively 1:100,0.25:100,0.3:100,3:100,0.5:
100;
4, incipient impregnation is handled
Copper-iron-manganese-nickel prepared by step 3-cerium salt maceration extract (209ml) spray arrives the accurate weighed catalyst of step 1
On carrier, rotation dipping carries out incipient impregnation processing, so that maceration extract, by carrier uniform adsorption, maceration extract substantially uniformity is inhaled
By the carrier for having adsorbed maceration extract standing 8h, (usually 3-12h divides maceration extract component uniformly on carrier after being attached on carrier
Cloth), load maceration extract carrier is made;Or
Copper-iron-manganese-nickel-cerium salt maceration extract (209ml) prepared by step 3 pours into the accurate weighed catalyst of step 1 and carries
In body, rotation dipping carries out incipient impregnation processing, so that maceration extract is by carrier uniform adsorption, the absorption of maceration extract substantially uniformity
By the carrier for having adsorbed maceration extract standing 8h, (usually 3-12h divides maceration extract component uniformly on carrier after on to carrier
Cloth), load maceration extract carrier is made;
5, it is dried
Load maceration extract carrier is laid in pallet, the baking oven that temperature is 120 DEG C (usually 100-120 DEG C) is put into
In, the dry 4h (usually >=2h, preferably 2-7h) at 120 DEG C;
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate keeps 1h under conditions of 300 DEG C from room temperature to 300 DEG C;Then again with the heating rate of 5 DEG C/min from
300 DEG C are warming up to 500 DEG C, and keep 3h at 500 DEG C;Then it is down to room temperature naturally from 500 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-
NiO-MnO2-CeO2/γ-Al2O3Catalyst).
In catalyst preparation process of the present invention, maturing temperature influences the property (such as activity etc.) and active component of catalyst
Dispersion degree, first segment maturing temperature control at 300-350 DEG C so that active component precursors are decomposed into corresponding oxidation in advance
Object.Second stage maturing temperature is controlled at 400-550 DEG C, is conducive to active component, carrier interaction, is formed optimal surface
Structure is firmly combined between active component and carrier.If temperature is higher than 550 DEG C, carrier γ-Al2O3Physical property may become
Change.Heating rate control is to avoid generating to guarantee catalyst thermally equivalent lower than 10 DEG C/min during calcination process
Big stress and the intensity for reducing catalyst.
Supported copper manufactured in the present embodiment, iron, nickel, manganese, cerium catalyst in the content of copper oxide be 1%, iron oxide
Content is 0.25%, and the content of nickel oxide is 0.3%, and the content of manganese oxide is 3%, and the content of cerium oxide is 0.5%.
3 catalyst preparation of embodiment
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, four water manganese acetates (33.8g), nine water ferric nitrates (5.1g), four water nickel acetates are sequentially added
(4.0g), cerous acetate (4.5g), a water copper acetate (10g) stir 30 minutes, are completely dissolved solid, add deionized water,
Until the total volume of mixed solution is 209ml, it is made maceration extract (i.e. copper-iron-manganese-nickel-cerium salt maceration extract), it is spare, wherein soaking
Copper acetate is converted into the quality of copper oxide (CuO) in stain liquid, ferric nitrate is converted into iron oxide (Fe2O3) quality, nickel acetate conversion
Manganese oxide (MnO is converted at the quality of nickel oxide (NiO), manganese acetate2) quality, cerous acetate be converted into cerium oxide (CeO2)
Quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, manganese oxide, the quality of cerium oxide and weighed carrier quality
The summation of (380g)) mass ratio be respectively 1:100,0.25:100,0.3:100,3:100,0.5:100;
4, incipient impregnation is handled
Copper-iron-manganese-nickel-cerium salt maceration extract (209ml) prepared by step 3 pours into the accurate weighed catalyst of step 1 and carries
In body, rotation dipping carries out incipient impregnation processing, so that maceration extract is by carrier uniform adsorption, the absorption of maceration extract substantially uniformity
By the carrier for having adsorbed maceration extract standing 10h, (usually 3-12h divides maceration extract component uniformly on carrier after on to carrier
Cloth), load maceration extract carrier is made;
5, it is dried
Load maceration extract carrier is laid in pallet, the baking oven that temperature is 110 DEG C (usually 100-120 DEG C) is put into
In, the dry 7h (usually >=2h, preferably 2-7h) at 110 DEG C;
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1h;Then again with the heating rate of 5 DEG C/min from
350 DEG C are warming up to 490 DEG C, and keep 3h at 490 DEG C;Then it is down to room temperature naturally from 490 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-
NiO-MnO2-CeO2/γ-Al2O3Catalyst).
Supported copper manufactured in the present embodiment, iron, nickel, manganese, cerium catalyst in the content of copper oxide be 1%, iron oxide
Content is 0.25%, and the content of nickel oxide is 0.3%, and the content of manganese oxide is 3%, and the content of cerium oxide is 0.5%.
4 catalyst preparation of embodiment
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, 50% manganese nitrate aqueous solution (32.9g), nine water ferric nitrates (6.1g), six water are sequentially added
Nickel nitrate (4.7g), cerium nitrate hexahydrate (2.0g), nitrate trihydrate copper (12.2g) stir 30 minutes, are completely dissolved solid, then plus
Enter deionized water, until the total volume of mixed solution is 209ml, maceration extract (i.e. copper-iron-manganese-nickel-cerium salt maceration extract) be made,
Spare, wherein copper nitrate is converted into the quality of copper oxide (CuO) in maceration extract, ferric nitrate is converted into iron oxide (Fe2O3) matter
Amount, nickel nitrate is converted into the quality of nickel oxide (NiO), manganese nitrate is converted into manganese oxide (MnO2) quality, cerous nitrate is converted into
Cerium oxide (CeO2) quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, manganese oxide, the quality of cerium oxide and title
The summation of the carrier quality (380g) taken) mass ratio be respectively 1:100,0.3:100,0.3:100,2:100,0.2:100;
4, incipient impregnation is handled
Copper-iron-manganese-nickel prepared by step 3-cerium salt maceration extract (209ml) spray arrives the accurate weighed catalyst of step 1
On carrier, rotation dipping carries out incipient impregnation processing, so that maceration extract, by carrier uniform adsorption, maceration extract substantially uniformity is inhaled
By the carrier for having adsorbed maceration extract standing 8h, (usually 3-12h divides maceration extract component uniformly on carrier after being attached on carrier
Cloth), load maceration extract carrier is made;
Or copper-iron-manganese-nickel-cerium salt the maceration extract (209ml) for preparing step 3 pours into the accurate weighed catalyst of step 1
In carrier, rotation dipping carries out incipient impregnation processing, so that maceration extract, by carrier uniform adsorption, maceration extract substantially uniformity is inhaled
By the carrier for having adsorbed maceration extract standing 8h, (usually 3-12h divides maceration extract component uniformly on carrier after being attached on carrier
Cloth), load maceration extract carrier is made;
5, it is dried
Load maceration extract carrier is laid in pallet, the baking oven that temperature is 120 DEG C (usually 100-120 DEG C) is put into
In, the dry 5h (usually >=2h, preferably 2-7h) at 120 DEG C;
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with 4.5 DEG C/min's during calcination process
Heating rate from room temperature to 300 DEG C, and under conditions of 300 DEG C under keep 1h;Then again with the heating speed of 4.5 DEG C/min
Rate is warming up to 460 DEG C from 300 DEG C, and keeps 5h at 460 DEG C;Then it is down to room temperature naturally from 460 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-
NiO-MnO2-CeO2/γ-Al2O3Catalyst).
Supported copper manufactured in the present embodiment, iron, nickel, manganese, cerium catalyst in the content of copper oxide be 1%, iron oxide
Content is 0.3%, and the content of nickel oxide is 0.3%, and the content of manganese oxide is 2%, and the content of cerium oxide is 0.2%.
5 catalyst preparation of embodiment
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, four water manganese acetates (22.5g), nine water ferric nitrates (6.1g), four water nickel acetates are sequentially added
(4.0g), cerium nitrate hexahydrate (5.3g), nitrate trihydrate copper (12.20g) stir 30 minutes, are completely dissolved solid, add
Ionized water is made maceration extract (i.e. copper-iron-manganese-nickel-cerium salt maceration extract) until the total volume of mixed solution is 209ml, spare,
Wherein copper nitrate is converted into the quality of copper oxide (CuO) in maceration extract, ferric nitrate is converted into iron oxide (Fe2O3) quality, acetic acid
Nickel is converted into the quality of nickel oxide (NiO), manganese acetate is converted into manganese oxide (MnO2) quality, cerous nitrate be converted into cerium oxide
(CeO2) quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, manganese oxide, cerium oxide quality and weighed load
The summation of weight (380g)) mass ratio be respectively 1:100,0.3:100,0.3:100,2:100,0.5:100;
4, incipient impregnation is handled
Copper-iron-manganese-nickel-cerium salt maceration extract (209ml) prepared by step 3 pours into the accurate weighed catalyst of step 1 and carries
In body, rotation dipping carries out incipient impregnation processing, so that maceration extract is by carrier uniform adsorption, the absorption of maceration extract substantially uniformity
By the carrier for having adsorbed maceration extract standing 12h, (usually 3-12h divides maceration extract component uniformly on carrier after on to carrier
Cloth), load maceration extract carrier is made;
5, it is dried
Load maceration extract carrier is laid in pallet, the baking oven that temperature is 120 DEG C (usually 100-120 DEG C) is put into
In, the dry 4h (usually >=2h, preferably 2-7h) at 120 DEG C;
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1h;Then again with the heating rate of 5 DEG C/min from
350 DEG C are warming up to 500 DEG C, and keep 3h at 500 DEG C;Then it is down to room temperature naturally from 500 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-
NiO-MnO2-CeO2/γ-Al2O3Catalyst).
Supported copper manufactured in the present embodiment, iron, nickel, manganese, cerium catalyst in the content of copper oxide be 1%, iron oxide
Content is 0.3%, and the content of nickel oxide is 0.3%, and the content of manganese oxide is 2%, and the content of cerium oxide is 0.5%.
6 catalyst preparation of embodiment
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, 50% manganese nitrate aqueous solution (32.9g), nine water ferric nitrates (18.2g), four water are sequentially added
Nickel acetate (13.3g), cerium nitrate hexahydrate (4.0g), nitrate trihydrate copper (6.1g) stir 30 minutes, are completely dissolved solid, then plus
Enter deionized water, until the total volume of mixed solution is 209ml, maceration extract (i.e. copper-iron-manganese-nickel-cerium salt maceration extract) be made,
Spare, wherein copper nitrate is converted into the quality of copper oxide (CuO) in maceration extract, ferric nitrate is converted into iron oxide (Fe2O3) matter
Amount, nickel acetate is converted into the quality of nickel oxide (NiO), manganese nitrate is converted into manganese oxide (MnO2) quality, cerous nitrate is converted into
Cerium oxide (CeO2) quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, manganese oxide, the quality of cerium oxide and title
The summation of the carrier quality (380g) taken) mass ratio be respectively 0.5:100,0.9:100,1:100,2:100,0.4:100;
4, incipient impregnation is handled
Copper-iron-manganese-nickel prepared by step 3-cerium salt maceration extract (209ml) spray arrives the accurate weighed catalyst of step 1
On carrier, rotation dipping carries out incipient impregnation processing, so that maceration extract, by carrier uniform adsorption, maceration extract substantially uniformity is inhaled
By the carrier for having adsorbed maceration extract standing 6h, (usually 3-12h divides maceration extract component uniformly on carrier after being attached on carrier
Cloth), load maceration extract carrier is made;
5, it is dried
Load maceration extract carrier is laid in pallet, the baking oven that temperature is 120 DEG C (usually 100-120 DEG C) is put into
In, the dry 5h (usually >=2h, preferably 2-7h) at 120 DEG C;
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 4 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1h;Then again with the heating rate of 4.5 DEG C/min
It is warming up to 475 DEG C from 350 DEG C, and keeps 4h at 475 DEG C;Then it is down to room temperature naturally from 475 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-
NiO-MnO2-CeO2/γ-Al2O3Catalyst).
Supported copper manufactured in the present embodiment, iron, nickel, manganese, cerium catalyst in the content of copper oxide be 0.5%, iron oxide
Content be 0.9%, the content of nickel oxide is 1%, and the content of manganese oxide is 2%, and the content of cerium oxide is 0.4%.
7 catalyst preparation of embodiment
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, four water manganese acetates (16.9g), nine water ferric nitrates (18.2g), four water nickel acetates are sequentially added
(13.3g), cerium nitrate hexahydrate (3.0g), nitrate trihydrate copper (6.1g) stir 30 minutes, are completely dissolved solid, add
Ionized water is made maceration extract (i.e. copper-iron-manganese-nickel-cerium salt maceration extract) until the total volume of mixed solution is 209ml, spare,
Wherein copper nitrate is converted into the quality of copper oxide (CuO) in maceration extract, ferric nitrate is converted into iron oxide (Fe2O3) quality, acetic acid
Nickel is converted into the quality of nickel oxide (NiO), manganese acetate is converted into manganese oxide (MnO2) quality, cerous nitrate be converted into cerium oxide
(CeO2) quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, manganese oxide, cerium oxide quality and weighed load
The summation of weight (380g)) mass ratio be respectively 0.5:100,0.9:100,1:100,1.5:100,0.3:100;
4, incipient impregnation is handled
Copper-iron-manganese-nickel prepared by step 3-cerium salt maceration extract (209ml) spray arrives the accurate weighed catalyst of step 1
On carrier, rotation dipping carries out incipient impregnation processing, so that maceration extract, by carrier uniform adsorption, maceration extract substantially uniformity is inhaled
By the carrier for having adsorbed maceration extract standing 9h, (usually 3-12h divides maceration extract component uniformly on carrier after being attached on carrier
Cloth), load maceration extract carrier is made;
5, it is dried
Load maceration extract carrier is laid in pallet, the baking oven that temperature is 120 DEG C (usually 100-120 DEG C) is put into
In, the dry 5h (usually >=2h, preferably 2-7h) at 120 DEG C;
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1.5h;Then again with the heating rate of 4 DEG C/min
It is warming up to 490 DEG C from 350 DEG C, and keeps 4h at 490 DEG C;Then it is down to room temperature naturally from 490 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-
NiO-MnO2-CeO2/γ-Al2O3Catalyst).
Supported copper manufactured in the present embodiment, iron, nickel, manganese, cerium catalyst in the content of copper oxide be 0.5%, iron oxide
Content be 0.9%, the content of nickel oxide is 1%, and the content of manganese oxide is 1.5%, and the content of cerium oxide is 0.3%.
Reference examples 1
Certain commercially available commodity ozone catalytic oxidation catalyst is chosen as reference examples 1, which prepared using mixing method,
Carrier is alumina globule, and active component is copper oxide.Ozone catalytic oxidation catalyst 4wt%CuO/ γ-Al2O3, partial size 3-
5mm。
Reference examples 2
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, four water manganese acetates (22.5g), nine water ferric nitrates (6.1g), four water nickel acetates are successively entered
(4.0g), cerium nitrate hexahydrate (19.9g), nitrate trihydrate copper (12.2g) stir 30 minutes, are completely dissolved solid, add
Ionized water is made maceration extract (i.e. copper-iron-manganese-nickel-cerium salt maceration extract) until the total volume of mixed solution is 209ml, spare,
Wherein copper nitrate is converted into the quality of copper oxide (CuO) in maceration extract, ferric nitrate is converted into iron oxide (Fe2O3) quality, acetic acid
Nickel is converted into the quality of nickel oxide (NiO), manganese acetate is converted into manganese oxide (MnO2) quality, cerous nitrate be converted into cerium oxide
(CeO2) quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, manganese oxide, cerium oxide quality and weighed load
The summation of weight (380g)) mass ratio be respectively 1:100,0.3:100,0.3:100,2:100,2:100;
4, incipient impregnation is handled
Copper-iron-manganese-nickel-cerium salt maceration extract (209ml) prepared by step 3 pours into the accurate weighed catalyst of step 1 and carries
In body, rotation dipping carries out incipient impregnation processing, so that maceration extract is by carrier uniform adsorption, the absorption of maceration extract substantially uniformity
By the carrier for having adsorbed maceration extract standing 10h, (usually 3-12h divides maceration extract component uniformly on carrier after on to carrier
Cloth), load maceration extract carrier is made;
5, it is dried
It is same as Example 4
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1h;Then again with the heating rate of 5 DEG C/min from
350 DEG C are warming up to 500 DEG C, and keep 4h at 500 DEG C;Then it is down to room temperature naturally from 500 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-
NiO-MnO2-CeO2/γ-Al2O3Catalyst).
This reference examples preparation supported copper, iron, nickel, manganese, cerium catalyst in copper oxide content be 1%, iron oxide
Content is 0.3%, and the content of nickel oxide is 0.3%, and the content of manganese oxide is 2%, and the content of cerium oxide is 2%.
Reference examples 3
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, four water manganese acetates (22.5g), nine water ferric nitrates (6.1g), four water nickel acetates are sequentially added
(4.0g), nitrate trihydrate copper (12.2g) stirs 30 minutes, is completely dissolved solid, adds deionized water, until mixing molten
The total volume of liquid is 209ml, maceration extract (i.e. copper-iron-manganese-nickel salt maceration extract) is made, spare, wherein copper nitrate changes in maceration extract
It is counted as the quality of copper oxide (CuO), ferric nitrate is converted into iron oxide (Fe2O3) quality, nickel acetate be converted into nickel oxide (NiO)
Quality, manganese acetate be converted into manganese oxide (MnO2) quality quality and catalyst total amount (i.e. copper oxide, iron oxide, oxidation
Nickel, manganese oxide quality and weighed carrier quality (380g) summation) mass ratio be respectively 1:100,0.3:100,
0.3:100,2:100;
4, incipient impregnation is handled
Copper-iron-manganese prepared by step 3-nickel salt maceration extract (209ml) spray is carried to the accurate weighed catalyst of step 1
On body, rotation dipping carries out incipient impregnation processing, so that maceration extract is by carrier uniform adsorption, the absorption of maceration extract substantially uniformity
By the carrier for having adsorbed maceration extract standing 10h, (usually 3-12h divides maceration extract component uniformly on carrier after on to carrier
Cloth), load maceration extract carrier is made;
5, it is dried
It is same as Example 4
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1h;Then again with the heating rate of 5 DEG C/min from
350 DEG C are warming up to 500 DEG C, and keep 3h at 500 DEG C;Then it is down to room temperature naturally from 500 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), manganese oxide (MnO2) catalyst (i.e. CuO-Fe2O3-NiO-MnO2/γ-
Al2O3Catalyst).
This reference examples preparation supported copper, iron, nickel, manganese catalyst in copper oxide content be 1%, the content of iron oxide
It is 0.3%, the content of nickel oxide is 0.3%, and the content of manganese oxide is 2%.
Reference examples 4
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, nine water ferric nitrates (6.1g), four water nickel acetates (4.0g), cerium nitrate hexahydrate are sequentially added
(2.0g), nitrate trihydrate copper (12.2g) stirs 30 minutes, is completely dissolved solid, adds deionized water, until mixing molten
The total volume of liquid is 209ml, maceration extract (i.e. copper-iron-nickel-cerium salt maceration extract) is made, spare, wherein copper nitrate changes in maceration extract
It is counted as the quality of copper oxide (CuO), ferric nitrate is converted into iron oxide (Fe2O3) quality, nickel acetate be converted into nickel oxide (NiO)
Quality, cerous nitrate be converted into cerium oxide (CeO2) quality and catalyst total amount (i.e. copper oxide, iron oxide, nickel oxide, oxidation
The summation of the quality of cerium and weighed carrier quality (380g)) mass ratio be respectively 1:100,0.3:100,0.3:100,
0.2:100;
4, incipient impregnation is handled
Copper-iron-nickel prepared by step 3-cerium salt maceration extract (209ml) spray is carried to the accurate weighed catalyst of step 1
On body, rotation dipping carries out incipient impregnation processing, so that maceration extract is by carrier uniform adsorption, the absorption of maceration extract substantially uniformity
By the carrier for having adsorbed maceration extract standing 10h, (usually 3-12h divides maceration extract component uniformly on carrier after on to carrier
Cloth), load maceration extract carrier is made;
5, it is dried
It is same as Example 4
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1h;Then again with the heating rate of 5 DEG C/min from
350 DEG C are warming up to 500 DEG C, and keep 3h at 500 DEG C;Then it is down to room temperature naturally from 500 DEG C, obtains loaded copper oxide
(CuO), iron oxide (Fe2O3), nickel oxide (NiO), cerium oxide (CeO2) catalyst (i.e. CuO-Fe2O3-NiO-CeO2/γ-
Al2O3Catalyst).
This reference examples preparation supported copper, iron, nickel, cerium catalyst in copper oxide content be 1%, the content of iron oxide
It is 0.3%, the content of nickel oxide is 0.3%, and the content of cerium oxide is 0.2%.
Reference examples 5
Steps 1 and 2 are same as Example 2;
3, maceration extract is prepared
Portions of de-ionized water is taken, four water manganese acetates (22.5g), four water nickel acetates (4.0g), cerium nitrate hexahydrate are sequentially added
(2.0g), nitrate trihydrate copper (12.2g) stirs 30 minutes, is completely dissolved solid, adds deionized water, until mixing molten
The total volume of liquid is 209ml, maceration extract (i.e. copper-nickel-manganese-cerium salt maceration extract) is made, spare, wherein copper nitrate changes in maceration extract
It is counted as the quality of copper oxide (CuO), nickel acetate is converted into the quality of nickel oxide (NiO), manganese acetate is converted into manganese oxide (MnO2)、
Cerous nitrate is converted into cerium oxide (CeO2) quality and catalyst total amount (the i.e. matter of copper oxide, nickel oxide, manganese oxide, cerium oxide
Amount and the summation of weighed carrier quality (380g)) mass ratio be respectively 1:100,0.3:100,2:100,0.2:100;
4, incipient impregnation is handled
Copper-nickel-manganese prepared by step 3 -- cerium salt maceration extract (209ml) pours into the accurate weighed catalyst carrier of step 1
In, rotation dipping carries out incipient impregnation processing, so that maceration extract, by carrier uniform adsorption, maceration extract substantially uniformity is adsorbed onto
By the carrier for having adsorbed maceration extract standing 10h, (usually 3-12h divides maceration extract component uniformly on carrier after on carrier
Cloth), load maceration extract carrier is made;
5, it is dried
It is same as Example 4
6, calcination process
Dried catalyst is placed in Muffle furnace and carries out calcination process, with the liter of 5 DEG C/min during calcination process
Warm rate from room temperature to 350 DEG C, and under conditions of 350 DEG C under keep 1h;Then again with the heating rate of 5 DEG C/min from
350 DEG C are warming up to 500 DEG C, and keep 4h at 500 DEG C;Then it is down to room temperature naturally from 500 DEG C, obtains loaded copper oxide, oxygen
Change catalyst (the i.e. CuO-NiO-MnO of nickel, manganese oxide, cerium oxide2-CeO2/γ-Al2O3Catalyst).
This reference examples preparation supported copper, nickel, manganese, cerium catalyst in iron oxide content be 1%, the content of nickel oxide
It is 0.3%, the content of manganese oxide is 2%, and the content of cerium oxide is 0.2%.
The catalytic ozonation purified treatment of 1 high salinity and chlorine wastewater from chemical industry of test example
The present invention evaluates the activity of catalyst in a manner of continuously flowing
Embodiment 2-7, reference examples 2-5 are respectively charged into internal diameter 30mm × height 800mm stainless steel column shaped reaction device
Catalyst (500mL) ozone catalytic oxidation catalyst of preparation, the commercial catalyst (500ml) of reference examples 1, then to reactor
It is inside passed through high salinity and chlorine organic wastewater and ozone, ozone is entered by aeration head by bottom, and waste water is added by the top of reactor,
Gas-liquid counter current contact;Wherein:
The water quality of high salinity and chlorine organic wastewater is as follows: COD 81mg/L, chloride ion content 6000mg/L, TDS
12000mg/L;
Flow of inlet water is 8mL/min.Ozone inlet gas concentration is 70mg/L, and ozone charge flow rate is 10mL/min.Water inlet stops
Stay time 60min.
Wastewater volume air speed 1h-1, ozone dosage 100mg/L, the water sampling after reacting 3h, 120h, measurement water outlet
COD value.
Wherein, according to the side of professional standard " the measurement chlorine correction method of HJ/T 70-2001 chemical oxygen demand of high-chloride wastewater "
Method measures the COD of waste water, and measurement result is as shown in table 1.
Calculate COD removal rate (η) according to formula (2): calculated result is as shown in table 1.
η=(C1-C2)/C1×100 (2)
In formula: η-COD removal rate, %;C1- influent COD, mg/L;C2- water outlet COD, mg/L.
The intensity test of the ozone catalytic oxidation catalyst of 2 high salinity and chlorine wastewater from chemical industry of test example
The method measurement 2-7 of the embodiment of the present invention of reference chemical standard " HG/T 3927-2007 industrial activated alumina ",
The compression strength of the catalyst of reference examples 1-5.Measurement result is as shown in table 1.
1. taking catalyst sample one to be measured, it is placed on the pressure-bearing top of intensity measuring device, presses startup button, until is broken into
Only, the reading in digital display field is write down, is repeated said determination 20 times.
2. compression strength is remembered with F, numerical value is indicated with N/, is calculated by formula (3)
In formula: Pi: the numerical value for the compression strength that each catalyst sample is measured, unit N;20: sample particle number.
The Contrast on effect of 1. different catalysts O3 catalytic oxidation high salinity and chlorine waste water of table
Claims (10)
1. a kind of wastewater from chemical industry catalytic ozonation catalysts for treating, characterized in that including catalyst carrier and active component,
Wherein the active constituent is the oxide of metallic copper, iron, nickel, manganese, cerium.
2. catalyst as described in claim 1, characterized in that the carrier selective oxidation aluminium, molecular sieve, haydite, zirconium oxide.
3. catalyst as claimed in claim 1 or 2, characterized in that metallic copper object is CuO, gold in the active component
Category ferriferous oxide is Fe2O3, metal nickel oxide be NiO, metal manganese oxide MnO2, metallic cerium oxide CeO2。
4. catalyst as claimed in claim 1 or 2, characterized in that the activity component metal Cu oxide and catalyst
Weight is (0.1-1.5): 100;The weight of metal ferriferous oxide and catalyst is (0.1-1.5): 100;Gold
The weight for belonging to nickel oxide and catalyst is (0.1-1.5): 100;Metal manganese oxide and the parts by weight of catalyst are matched
Than for (0.5-3): 100;The weight of metallic cerium oxide and catalyst is (0.05-0.7): 100.
5. a kind of preparation method of catalytic ozonation processing wastewater from chemical industry catalyst, characterized in that including following sequence into
Capable step:
1) water absorption rate (Y, %) of carrier is measured;
2) catalyst carrier of accurate weighing certain mass, and the water absorption rate measured according to step 1) calculate the weighed catalysis of institute
Agent carrier carries out the volume of maceration extract required when incipient impregnation processing;
3) active component precursors are added to the water after dissolution, add water the bodies such as the catalyst carrier being calculated into step 2)
The volume of required maceration extract, is made precursor maceration extract when product impregnation;Wherein, the active component precursors select metal
Copper, iron, nickel, manganese, cerium salt compounds;
4) active component precursors maceration extract prepared by step 3) is carried on by step 2) weighing using incipient impregnation facture
In carrier;
5) carrier after impregnation is successively dried, calcination process.
6. preparation method as claimed in claim 5, characterized in that the aluminium of carrier selective oxidation described in step 1), molecular sieve, pottery
Grain, zirconium oxide.
7. preparation method as claimed in claim 5, characterized in that the salt compounds of metal described in step 3) are nitric acid
Salt, acetate or formates.
8. preparation method as claimed in claim 5, characterized in that before the active component being add to deionized water in step 3)
The salt compounds of body metallic copper are converted into the carrier and active component precursors that the quality after metal oxide and step 2) weigh
The ratio of the summation of the quality for the metal oxide being converted into is (0.1-1.5): 100;The salt compounds of metallic iron are converted into
The quality for the metal oxide that the carrier and active component precursors that quality and step 2) after metal oxide weigh are converted into
The ratio of summation is (0.1-1.5): 100;The salt compounds of metallic nickel are converted into quality and step 2) after metal oxide
The ratio of the summation of the quality for the metal oxide that the carrier and active component precursors of weighing are converted into is (0.1-1.5): 100;
The salt compounds of manganese metal are converted into the carrier that the quality after metal oxide is weighed with step 2) and active component precursors change
The ratio of the summation of the quality for the metal oxide being counted as is (0.5-3): 100;The salt compounds of metallic cerium are converted into metal
The summation of the quality for the metal oxide that the carrier and active component precursors that quality and step 2) after oxide weigh are converted into
Ratio be (0.05-0.7): 100.
9. preparation method as claimed in claim 5, characterized in that active component precursors described in step 3) are converted into metal oxygen
The quality for the metal oxide that the carrier and active component precursors that quality sum after compound and step 2) weigh are converted into it is total
The ratio of sum is (3-6): 100.
10. preparation method as claimed in claim 5, characterized in that drying temperature described in step 5) is 100-120 DEG C;It is dry
At least 2h of dry time.
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