JP2018158316A - Complex of photocatalyst and adsorbent - Google Patents
Complex of photocatalyst and adsorbent Download PDFInfo
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- JP2018158316A JP2018158316A JP2017058023A JP2017058023A JP2018158316A JP 2018158316 A JP2018158316 A JP 2018158316A JP 2017058023 A JP2017058023 A JP 2017058023A JP 2017058023 A JP2017058023 A JP 2017058023A JP 2018158316 A JP2018158316 A JP 2018158316A
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- visible light
- adsorbent
- responsive photocatalyst
- light responsive
- photocatalyst
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- 239000003463 adsorbent Substances 0.000 title claims abstract description 79
- 239000011941 photocatalyst Substances 0.000 title claims description 50
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 130
- 239000000377 silicon dioxide Substances 0.000 claims abstract description 65
- 239000010457 zeolite Substances 0.000 claims abstract description 64
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 63
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 63
- QGLKJKCYBOYXKC-UHFFFAOYSA-N nonaoxidotritungsten Chemical compound O=[W]1(=O)O[W](=O)(=O)O[W](=O)(=O)O1 QGLKJKCYBOYXKC-UHFFFAOYSA-N 0.000 claims abstract description 50
- 229910001930 tungsten oxide Inorganic materials 0.000 claims abstract description 50
- 239000013078 crystal Substances 0.000 claims abstract description 9
- 239000000203 mixture Substances 0.000 claims abstract description 9
- 208000008842 sick building syndrome Diseases 0.000 claims abstract description 9
- 239000011164 primary particle Substances 0.000 claims abstract description 6
- 239000011148 porous material Substances 0.000 claims abstract description 5
- 239000000126 substance Substances 0.000 claims description 18
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical group [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims description 14
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims description 12
- 229910018072 Al 2 O 3 Inorganic materials 0.000 claims description 11
- 229910004298 SiO 2 Inorganic materials 0.000 claims description 11
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims description 10
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 claims description 9
- BDAGIHXWWSANSR-UHFFFAOYSA-N methanoic acid Natural products OC=O BDAGIHXWWSANSR-UHFFFAOYSA-N 0.000 claims description 8
- 229910052697 platinum Inorganic materials 0.000 claims description 7
- FYGHSUNMUKGBRK-UHFFFAOYSA-N 1,2,3-trimethylbenzene Chemical compound CC1=CC=CC(C)=C1C FYGHSUNMUKGBRK-UHFFFAOYSA-N 0.000 claims description 6
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 6
- YNQLUTRBYVCPMQ-UHFFFAOYSA-N Ethylbenzene Chemical compound CCC1=CC=CC=C1 YNQLUTRBYVCPMQ-UHFFFAOYSA-N 0.000 claims description 6
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 5
- 229910052802 copper Inorganic materials 0.000 claims description 5
- 239000010949 copper Substances 0.000 claims description 5
- 229910052763 palladium Inorganic materials 0.000 claims description 5
- OSWFIVFLDKOXQC-UHFFFAOYSA-N 4-(3-methoxyphenyl)aniline Chemical compound COC1=CC=CC(C=2C=CC(N)=CC=2)=C1 OSWFIVFLDKOXQC-UHFFFAOYSA-N 0.000 claims description 4
- IKHGUXGNUITLKF-XPULMUKRSA-N acetaldehyde Chemical compound [14CH]([14CH3])=O IKHGUXGNUITLKF-XPULMUKRSA-N 0.000 claims description 4
- 150000001875 compounds Chemical class 0.000 claims description 4
- 235000019253 formic acid Nutrition 0.000 claims description 4
- 150000004820 halides Chemical class 0.000 claims description 4
- 239000001257 hydrogen Substances 0.000 claims description 4
- 229910052739 hydrogen Inorganic materials 0.000 claims description 4
- 150000003839 salts Chemical class 0.000 claims description 4
- XYHKNCXZYYTLRG-UHFFFAOYSA-N 1h-imidazole-2-carbaldehyde Chemical compound O=CC1=NC=CN1 XYHKNCXZYYTLRG-UHFFFAOYSA-N 0.000 claims description 3
- GWYFCOCPABKNJV-UHFFFAOYSA-M 3-Methylbutanoic acid Natural products CC(C)CC([O-])=O GWYFCOCPABKNJV-UHFFFAOYSA-M 0.000 claims description 3
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 3
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- 229910021529 ammonia Inorganic materials 0.000 claims description 3
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- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims description 3
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- 239000008096 xylene Substances 0.000 claims description 3
- 125000004435 hydrogen atom Chemical group [H]* 0.000 claims description 2
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- 230000004044 response Effects 0.000 claims description 2
- 239000002131 composite material Substances 0.000 abstract description 9
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 abstract description 6
- 239000000463 material Substances 0.000 abstract description 3
- 229910052681 coesite Inorganic materials 0.000 abstract 1
- 229910052593 corundum Inorganic materials 0.000 abstract 1
- 229910052906 cristobalite Inorganic materials 0.000 abstract 1
- 235000012239 silicon dioxide Nutrition 0.000 abstract 1
- 229910052682 stishovite Inorganic materials 0.000 abstract 1
- 229910052905 tridymite Inorganic materials 0.000 abstract 1
- 229910001845 yogo sapphire Inorganic materials 0.000 abstract 1
- IKHGUXGNUITLKF-UHFFFAOYSA-N Acetaldehyde Chemical compound CC=O IKHGUXGNUITLKF-UHFFFAOYSA-N 0.000 description 40
- 239000002245 particle Substances 0.000 description 31
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical group O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 23
- 230000000052 comparative effect Effects 0.000 description 16
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 15
- 239000012855 volatile organic compound Substances 0.000 description 13
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 description 12
- 238000001179 sorption measurement Methods 0.000 description 11
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- 239000007789 gas Substances 0.000 description 9
- 238000000034 method Methods 0.000 description 9
- 239000011324 bead Substances 0.000 description 8
- 229910052751 metal Inorganic materials 0.000 description 8
- 230000001699 photocatalysis Effects 0.000 description 8
- 238000012360 testing method Methods 0.000 description 8
- 150000001299 aldehydes Chemical class 0.000 description 7
- 239000001569 carbon dioxide Substances 0.000 description 7
- 229910002092 carbon dioxide Inorganic materials 0.000 description 7
- 239000003054 catalyst Substances 0.000 description 7
- 238000000576 coating method Methods 0.000 description 7
- 239000006185 dispersion Substances 0.000 description 7
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- 238000010298 pulverizing process Methods 0.000 description 7
- 239000000725 suspension Substances 0.000 description 7
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 6
- 239000011248 coating agent Substances 0.000 description 6
- 238000000354 decomposition reaction Methods 0.000 description 6
- 235000019645 odor Nutrition 0.000 description 6
- 238000006864 oxidative decomposition reaction Methods 0.000 description 6
- 230000003197 catalytic effect Effects 0.000 description 5
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- 238000000227 grinding Methods 0.000 description 5
- 235000021190 leftovers Nutrition 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 5
- 239000003973 paint Substances 0.000 description 5
- 239000004408 titanium dioxide Substances 0.000 description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 4
- 239000003795 chemical substances by application Substances 0.000 description 4
- 230000007423 decrease Effects 0.000 description 4
- 238000009826 distribution Methods 0.000 description 4
- 238000010438 heat treatment Methods 0.000 description 4
- 238000009413 insulation Methods 0.000 description 4
- 239000010813 municipal solid waste Substances 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- WUPHOULIZUERAE-UHFFFAOYSA-N 3-(oxolan-2-yl)propanoic acid Chemical compound OC(=O)CCC1CCCO1 WUPHOULIZUERAE-UHFFFAOYSA-N 0.000 description 3
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 description 3
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 description 3
- 239000000853 adhesive Substances 0.000 description 3
- 230000001070 adhesive effect Effects 0.000 description 3
- 229910052980 cadmium sulfide Inorganic materials 0.000 description 3
- 239000000571 coke Substances 0.000 description 3
- 239000007771 core particle Substances 0.000 description 3
- 238000004332 deodorization Methods 0.000 description 3
- 238000011156 evaluation Methods 0.000 description 3
- 150000004679 hydroxides Chemical class 0.000 description 3
- 150000002736 metal compounds Chemical class 0.000 description 3
- -1 oxides Chemical class 0.000 description 3
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- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 2
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 description 2
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 2
- 231100000597 Sick building syndrome Toxicity 0.000 description 2
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 2
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 2
- 230000001133 acceleration Effects 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 238000004378 air conditioning Methods 0.000 description 2
- 238000004887 air purification Methods 0.000 description 2
- 229910052782 aluminium Inorganic materials 0.000 description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 2
- 150000001491 aromatic compounds Chemical class 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- XAYGUHUYDMLJJV-UHFFFAOYSA-Z decaazanium;dioxido(dioxo)tungsten;hydron;trioxotungsten Chemical compound [H+].[H+].[NH4+].[NH4+].[NH4+].[NH4+].[NH4+].[NH4+].[NH4+].[NH4+].[NH4+].[NH4+].O=[W](=O)=O.O=[W](=O)=O.O=[W](=O)=O.O=[W](=O)=O.O=[W](=O)=O.O=[W](=O)=O.[O-][W]([O-])(=O)=O.[O-][W]([O-])(=O)=O.[O-][W]([O-])(=O)=O.[O-][W]([O-])(=O)=O.[O-][W]([O-])(=O)=O.[O-][W]([O-])(=O)=O XAYGUHUYDMLJJV-UHFFFAOYSA-Z 0.000 description 2
- 230000001877 deodorizing effect Effects 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 2
- 229910052737 gold Inorganic materials 0.000 description 2
- 239000010931 gold Substances 0.000 description 2
- 229910052741 iridium Inorganic materials 0.000 description 2
- GKOZUEZYRPOHIO-UHFFFAOYSA-N iridium atom Chemical compound [Ir] GKOZUEZYRPOHIO-UHFFFAOYSA-N 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 239000010806 kitchen waste Substances 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 229910052750 molybdenum Inorganic materials 0.000 description 2
- 239000011733 molybdenum Substances 0.000 description 2
- 229910052759 nickel Inorganic materials 0.000 description 2
- 229910052758 niobium Inorganic materials 0.000 description 2
- 239000010955 niobium Substances 0.000 description 2
- GUCVJGMIXFAOAE-UHFFFAOYSA-N niobium atom Chemical compound [Nb] GUCVJGMIXFAOAE-UHFFFAOYSA-N 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 239000011347 resin Substances 0.000 description 2
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- 229910052709 silver Inorganic materials 0.000 description 2
- 239000004332 silver Substances 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- ZNOKGRXACCSDPY-UHFFFAOYSA-N tungsten trioxide Chemical compound O=[W](=O)=O ZNOKGRXACCSDPY-UHFFFAOYSA-N 0.000 description 2
- 206010011224 Cough Diseases 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 239000002879 Lewis base Substances 0.000 description 1
- XEMCCEZXLRCGOZ-UHFFFAOYSA-H O.O.O.O.O.O.Cl[Pt](Cl)(Cl)(Cl)(Cl)Cl Chemical compound O.O.O.O.O.O.Cl[Pt](Cl)(Cl)(Cl)(Cl)Cl XEMCCEZXLRCGOZ-UHFFFAOYSA-H 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- 229910019142 PO4 Inorganic materials 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 1
- PTFCDOFLOPIGGS-UHFFFAOYSA-N Zinc dication Chemical compound [Zn+2] PTFCDOFLOPIGGS-UHFFFAOYSA-N 0.000 description 1
- 230000009471 action Effects 0.000 description 1
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- 230000000274 adsorptive effect Effects 0.000 description 1
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- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
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Abstract
Description
本発明は、光触媒と吸着剤との複合体に関する。
詳細には、本発明は、可視光応答型で光触媒活性が高い酸化タングステンとハイシリカゼオライトとの複合体に関する。さらに詳細には、酸化タングステンとハイシリカゼオライトとの複合体である可視光応答型光触媒−吸着剤複合体に関する。
The present invention relates to a composite of a photocatalyst and an adsorbent.
Specifically, the present invention relates to a composite of tungsten oxide and high silica zeolite having a visible light response type and high photocatalytic activity. More specifically, the present invention relates to a visible light responsive photocatalyst-adsorbent complex which is a complex of tungsten oxide and high silica zeolite.
近年、日本における住宅は、高湿・高温に強い土壁・漆喰を用いた伝統的木造建築から、アルミサッシ製窓、断熱性および/または遮音性が高い壁を用い、耐震性に優れ、冷暖房の省エネ効果が高く、気密性が高い1戸建て住宅および/またはマンションへと変化してきた。 In recent years, houses in Japan have excellent earthquake resistance, air conditioning and heating, using aluminum sash windows, walls with high heat insulation and / or sound insulation, from traditional wooden buildings using earth walls and plaster resistant to high humidity and high temperature. It has been changed to single-family houses and / or condominiums with high energy-saving effects and high airtightness.
これらの住宅および/またはマンションでは、その気密性が高いが故に、壁紙、室内塗装、建具および家具などから発生した揮発性有機化合物(VOC)および/または台所のごみ、残飯もしくはトイレから発生し得る悪臭が原因と言われる、現代病であるシックハウス症候群の発症が問題になってきている。 In these houses and / or condominiums, because of their high airtightness, they can be generated from volatile organic compounds (VOC) generated from wallpaper, interior paint, joinery and furniture and / or kitchen waste, leftovers or toilets. The onset of sick house syndrome, which is a modern disease, which is said to be caused by malodor, has become a problem.
上記の揮発性有機化合物は、いずれも温度が上がると気化し易くなり、揮発量が増える性質を有している。そこで、日本のシックハウス症候群の名称が由来し、シックビルディング症候群と称され、室内で塗料を多く使うアメリカでは、その対策として、窓を閉め切り、暖房器具で、室温を30〜40℃に程度に温め、時々換気して室内の空気を入れ替えながら3日間ぐらいかけて化学物質を蒸し出すベイクアウト(加熱)法により、シックビルディング症候群の原因物質を処理・除去している。 Any of the above volatile organic compounds has a property of being easily vaporized when the temperature rises and increasing the amount of volatilization. Therefore, the name of Japanese sick house syndrome is derived, and it is called sick building syndrome. In the United States where a lot of paint is used indoors, as a countermeasure, the window is closed and the room temperature is raised to 30-40 ° C with a heater. The causative substance of sick building syndrome is treated and removed by baking out (heating) method, in which the chemicals are vaporized over about 3 days with occasional ventilation and replacement of indoor air.
しかしながら、このベイクアウト法は、塗料に対しては効果があるものの、複数枚の板が張り合わされた層からなる合板や厚みがあるビニールクロス等から発生するホルムアルデヒド等には、殆ど効果がないことが知られている。 However, although this bake-out method is effective for paint, it is hardly effective for formaldehyde generated from plywood consisting of a laminate of multiple sheets or thick vinyl cloth. It has been known.
上記の問題を解決するために、近年、脱臭剤および消臭剤とともに、臭い物質を光触媒で分解することが活発に研究されている。
特許文献1は、活性炭表面に光触媒を担持させ、紫外線ランプ等を用いて光触媒を励起させ、臭気成分を分解することを開示しているが、該光触媒が酸化チタンであることも開示している。
In order to solve the above problems, in recent years, active research has been conducted on the decomposition of odorous substances with a photocatalyst together with a deodorizing agent and a deodorizing agent.
Patent Document 1 discloses that a photocatalyst is supported on the surface of activated carbon, and the photocatalyst is excited using an ultraviolet lamp or the like to decompose odor components, but also discloses that the photocatalyst is titanium oxide. .
特許文献2は、光触媒と吸着剤とをバインダーを用いて塗料化した空気浄化塗料であって、前記吸着剤としてシリカ/アルミナ比が5.6以上92以下のハイシリカ合成ハイシリカゼオライトH型ZSM5を用いた光触媒を用いた空気浄化塗料を開示しているが、該光触媒が酸化チタンであることも開示している。 Patent Document 2 is an air purification paint obtained by coating a photocatalyst and an adsorbent with a binder. As the adsorbent, high silica synthetic high silica zeolite H-type ZSM5 having a silica / alumina ratio of 5.6 to 92 is used. Although the air purification coating using the used photocatalyst is disclosed, it is also disclosed that the photocatalyst is titanium oxide.
特許文献3は、気相中の揮発性芳香族化合物を分解するための光触媒体であって、酸化タングステン粒子を主成分として含有し、前記酸化タングステン粒子の表面を酸化チタン粒子で被覆されており、前記酸化チタン粒子の被覆量が、前記酸化タングステン粒子100質量部に対して、チタン換算で3〜45質量部であることを特徴とする揮発性芳香族化合物分解用光触媒体を開示している。 Patent Document 3 is a photocatalyst for decomposing a volatile aromatic compound in a gas phase, containing tungsten oxide particles as a main component, and the surface of the tungsten oxide particles being coated with titanium oxide particles. The photocatalyst for volatile aromatic compound decomposition is disclosed, wherein the coating amount of the titanium oxide particles is 3 to 45 parts by mass in terms of titanium with respect to 100 parts by mass of the tungsten oxide particles. .
また、特許文献4は、酸化タングステンを含むコア粒子と、上記コア粒子の表面に担持された助触媒を含む光触媒において、ハロゲンがドープされている光触媒材料を開示している。さらに、特許文献4は、上記コア粒子及び助触媒の表面全体を被覆するシェル層を備え、このシェル層が酸化チタンから構成されていることを開示している。 Patent Document 4 discloses a photocatalytic material in which halogen is doped in a photocatalyst including a core particle containing tungsten oxide and a cocatalyst supported on the surface of the core particle. Further, Patent Document 4 discloses that a shell layer covering the entire surfaces of the core particles and the promoter is provided, and the shell layer is made of titanium oxide.
さらに、非特許文献1は、酸化チタン/ZSM−5ゼオライト光触媒によるアセトアルデヒドの完全酸化分解反応に関して記載している。 Furthermore, Non-Patent Document 1 describes a complete oxidative decomposition reaction of acetaldehyde with a titanium oxide / ZSM-5 zeolite photocatalyst.
上記のように、従来光触媒と吸着剤とから構成される分解・浄化型触媒には、酸化チタンそのものが触媒として、または被覆剤として用いられている。
この酸化チタンは、近年光照射による自浄(セルフクリーニング)作用を有する触媒として知られており、この触媒を含む製品が開発され、トンネル内壁用塗装やビルの外壁塗装、テントおよびサイドミラー等にも用いられている。
As described above, titanium oxide itself is used as a catalyst or a coating agent in a decomposition / purification type catalyst composed of a conventional photocatalyst and an adsorbent.
This titanium oxide is known as a catalyst having a self-cleaning action by light irradiation in recent years, and a product containing this catalyst has been developed, and it is applied to tunnel inner wall painting, building outer wall painting, tents, side mirrors, etc. It is used.
しかしながら、酸化チタンは、紫外線には活性を示すが太陽光の大部分を占める可視光を殆ど吸収せず、可視光による触媒活性が弱く、紫外光ではないと自浄作用を十分発揮できないという問題も知られている。
そこで本発明は、紫外線のような高エネルギーの限られた光線ではなく、太陽光を主として構成する可視光で活性化される触媒、すなわち可視光応答型光触媒と吸着剤との複合化物、即ち、可視光応答型光触媒−吸着剤複合体の提供を課題とする。
However, titanium oxide is active in ultraviolet rays, but hardly absorbs visible light that occupies most of sunlight, has weak catalytic activity due to visible light, and can not exhibit its self-cleaning effect sufficiently if it is not ultraviolet light. Are known.
Therefore, the present invention is not a high-energy limited light beam such as ultraviolet rays but a catalyst activated by visible light mainly comprising sunlight, that is, a composite of a visible light responsive photocatalyst and an adsorbent, An object is to provide a visible light responsive photocatalyst-adsorbent complex.
そこで、本発明らは、上記の課題を解決するために鋭意研究を重ねた結果、揮発性有機化合物を、特定の金属酸化物−吸着剤複合体が吸着し、可視光の照射により分解することを見出し、本研究を完成するに至った。 Therefore, as a result of intensive studies to solve the above-mentioned problems, the present inventors have found that a volatile organic compound is adsorbed by a specific metal oxide-adsorbent complex and decomposed by irradiation with visible light. And led to the completion of this study.
しかるに、本発明によれば、酸化タングステンおよびハイシリカゼオライトが複合していることを特徴とする可視光応答型光触媒−吸着剤複合体が提供される。 However, according to the present invention, there is provided a visible light responsive photocatalyst-adsorbent complex characterized in that tungsten oxide and high silica zeolite are complexed.
また、本発明によれば、前記吸着剤が、SiO2/Al2O3組成比1200〜2200を有するハイシリカゼオライトである前記の可視光応答型光触媒−吸着剤複合体が提供される。 Further, according to the present invention, the adsorbent, wherein the visible-light-responsive photocatalyst is a high silica zeolite having a SiO 2 / Al 2 O 3 composition ratio 1200-2200 - adsorbent complex is provided.
また、本発明によれば、前記吸着剤が、ベータまたはZSM−5結晶形を有する前記の可視光応答型光触媒−吸着剤複合体が提供される。 Further, according to the present invention, there is provided the visible light responsive photocatalyst-adsorbent complex, wherein the adsorbent has a beta or ZSM-5 crystal form.
また、本発明によれば、前記吸着剤が、水素型ハイシリカゼオライトである前記の可視光応答型光触媒−吸着剤複合体が提供される。 Moreover, according to this invention, the said visible light responsive type photocatalyst-adsorbent complex whose said adsorbent is a hydrogen type high silica zeolite is provided.
また、本発明によれば、前記吸着剤が、細孔径5Å以上7Å未満を有する前記の可視光応答型光触媒−吸着剤複合体が提供される。 In addition, according to the present invention, there is provided the visible light responsive photocatalyst-adsorbent complex, wherein the adsorbent has a pore diameter of 5 mm or more and less than 7 mm.
また、本発明によれば、前記酸化タングステンが、一次粒径5〜100nmを有する前記の可視光応答型光触媒−吸着剤複合体が提供される。 In addition, according to the present invention, there is provided the visible light responsive photocatalyst-adsorbent complex, wherein the tungsten oxide has a primary particle size of 5 to 100 nm.
また、本発明によれば、前記ハイシリカゼオライトが、前記酸化タングステンの重量に対して10〜80重量%添加されている前記の可視応答型光触媒−吸着剤複合体が提供される。 Moreover, according to this invention, the said visible response type photocatalyst-adsorbent composite_body | complex to which the said high silica zeolite is added 10 to 80weight% with respect to the weight of the said tungsten oxide is provided.
また、本発明によれば、前記可視光応答型光触媒が、さらに助触媒を担持している前記の可視光応答型光触媒−吸着剤複合体が提供される。 In addition, according to the present invention, there is provided the visible light responsive photocatalyst-adsorbent complex in which the visible light responsive photocatalyst further supports a cocatalyst.
また、本発明によれば、前記助触媒が、白金、パラジウムまたは銅、そのハロゲン化物、酸化物、水酸化物または塩であり、酸化タングステンの重量に対して0.01〜3重量%添加されている前記の可視光応答型光触媒−吸着剤複合体が提供される。 According to the present invention, the promoter is platinum, palladium or copper, a halide, oxide, hydroxide or salt thereof, and is added in an amount of 0.01 to 3% by weight based on the weight of tungsten oxide. The visible light responsive photocatalyst-adsorbent complex is provided.
また、本発明によれば、前記可視光応答型光触媒−吸着剤複合体が、シックハウス症候群または家庭内悪臭の原因物質を吸着し、分解する前記の可視光応答型光触媒−吸着剤複合体が提供される。 In addition, according to the present invention, there is provided the visible light responsive photocatalyst-adsorbent complex, wherein the visible light responsive photocatalyst-adsorbent complex adsorbs and decomposes a causative substance of sick house syndrome or home odor. Is done.
さらに、本発明によれば、前記原因物質が、ホルムアルデヒド、アセトアルデヒド、ギ酸、酢酸、トルエン、キシレン、トリメチルベンゼン、エチルベンゼン、アンモニア、アミン、メルカプタン、硫化水素およびイソ吉草酸等からなる群に含まれる1以上の化合物である前記の可視光応答型光触媒−吸着剤複合体が提供される。 Furthermore, according to the present invention, the causative substance is included in the group consisting of formaldehyde, acetaldehyde, formic acid, acetic acid, toluene, xylene, trimethylbenzene, ethylbenzene, ammonia, amine, mercaptan, hydrogen sulfide, and isovaleric acid 1 The visible light responsive photocatalyst-adsorbent complex which is the above compound is provided.
本発明による可視光応答型光触媒−吸着剤複合体は、1戸建て、低層および高層マンションまたは建築物における居住空間、オフィス空間および学校、役場、役所、公会堂などの公共的建築物の室内空間ならびに自家用車、自動車、バスまたは列車の車内空間または船舶もしくは航空機などの客室空間において、壁紙、室内塗装、建具および家具などから発生し得る揮発性有機化合物(VOC)および/または台所または炊事場のごみか、残飯から発生し得る悪臭等を吸着し、室内照明の光により分解できる。 The visible light responsive photocatalyst-adsorbent complex according to the present invention is used for residential spaces, office spaces, and indoor spaces of public buildings such as schools, government offices, public halls, and private houses in single-family, low-rise and high-rise apartments or buildings. Volatile organic compounds (VOC) that can be generated from wallpaper, interior painting, fittings, furniture, etc. in the interior space of cars, automobiles, buses or trains, or cabin spaces such as ships or airplanes, or kitchen or kitchen waste It absorbs bad odors and the like that can be generated from leftover rice and can be decomposed by light from room lighting.
また、本発明による可視光応答型光触媒−吸着剤複合体は、繰り返し使用した場合の吸着機能、酸化分解機能(光触媒機能)が優れ、長期間に亘り使用できる。
したがって、ゴミ箱、残飯に用いるか、空気清浄機、エアコンのフィルターに用いるか、室内または車内で用いるスプレー剤、壁紙への塗布剤、あるいは繊維に練り込むことで衣類、寝具、カーテンまたはカーペットに使用できる。さらに、樹脂に添加するか、成型後の樹脂をコーティングしてトイレ用品やゴミ箱などに用いることができる。
Further, the visible light responsive photocatalyst-adsorbent complex according to the present invention has an excellent adsorption function and oxidative decomposition function (photocatalytic function) when used repeatedly, and can be used for a long period of time.
Therefore, it is used for clothes, bedding, curtains or carpets by being used for trash bins, leftovers, filters for air purifiers, air conditioners, sprays used indoors or in cars, wallpaper coatings, or kneaded into fibers. it can. Further, it can be added to the resin or coated with the molded resin and used for toilet articles, trash cans and the like.
本願明細書において用いられる用語「シックハウス症候群」とは、新築したばかりの家や、リフォームしたばかりの家、または職場が新しいビルに引っ越した途端、室内に入ると気分が悪くなる、だるい、のどや鼻の奥が痛い、目がチカチカする、咳が出て、体の調子が悪くなる比較的新しい症状を意味する。
家族の中でも主婦や幼児に起こる確率が高く、家にいる時間が長いこと、体質的に抵抗力が弱いこと等がその理由として挙げられている。
As used herein, the term “sick house syndrome” refers to a newly built home, a home that has just been remodeled, or a workplace that has moved to a new building, which makes you feel sick when you enter the room. It means a relatively new symptom that causes pain in the back of the nose, flickering eyes, coughing, and physical condition.
Among the family members, there are high probabilities that happen to housewives and infants, and the reason for this is that the time spent at home is long and the resistance to physical constitution is weak.
上記のシックハウス症候群は、アルミサッシ製窓、金属製扉、断熱性および/または遮音性が高い壁を用い、耐震性に優れ、冷暖房の省エネ効果が高く、気密性が高い1戸建て住宅、低層および/または高層マンションを含む建築物における居住空間、オフィス空間および学校、役場、役所、公会堂などの公共的室内空間ならびに自家用車、自動車、バスまたは列車の車内空間または船舶もしくは航空機などの客室空間においては、高い気密性が故に、壁紙、特に壁紙の粘着剤、室内塗装、建具および家具などから発生し得る揮発性有機化合物(VOC)および/または台所、炊事場のゴミや残飯もしくはトイレから発生し得る悪臭が原因となると言われている。 The above sick house syndrome uses aluminum sash windows, metal doors, walls with high heat insulation and / or sound insulation, excellent earthquake resistance, high energy-saving effect of air conditioning and heating, high-tightness detached houses, low-rise buildings and In residential spaces, office spaces and public spaces in buildings including high-rise apartments, public spaces such as schools, government offices, government offices and public halls, and cabin spaces such as private cars, cars, buses or trains, or cabins or aircraft Because of its high air tightness, it can be generated from wallpaper, especially volatile organic compounds (VOC) that can be generated from wallpaper adhesives, indoor coatings, joinery and furniture, etc. and / or from kitchen, kitchen trash, leftovers or toilets It is said that bad odor is the cause.
上記の壁紙、壁紙の粘着剤、室内塗装、建具および家具などから発生し得る揮発性有機化学物質としては、ホルムアルデヒド、アセトアルデヒド、ギ酸、酢酸、トルエン、キシレン、トリメチルベンゼン、エチルベンゼン等が挙げられる。 Examples of volatile organic chemical substances that can be generated from the above wallpaper, wallpaper adhesive, indoor coating, furniture and furniture include formaldehyde, acetaldehyde, formic acid, acetic acid, toluene, xylene, trimethylbenzene, and ethylbenzene.
また、台所、炊事場のゴミ、残飯またはトイレから発生し得る悪臭の成分としての化学物質としては、アンモニア、アミン、メルカプタン、硫化水素およびイソ吉草酸等が挙げられる。 Moreover, ammonia, an amine, a mercaptan, hydrogen sulfide, isovaleric acid, etc. are mentioned as a chemical substance as a malodorous component which can generate | occur | produce from the garbage of kitchen, a kitchen, leftovers, or a toilet.
可視光応答型光触媒
上記の揮発性有機化合物および/または悪臭もしくは生活臭の原因物質の吸着・酸化的分解のために用いられる、本発明による可視光応答型光触媒としては、二酸化チタン(酸化チタン、TiO2)、酸化亜鉛(ZnO)、硫化カドミウム(CdS)および酸化タングステン(WO3)が挙げられる。これら光触媒のそれぞれの有機化合物の分解能力には、さほど大きな差はないと言われている。
Visible Light Responsive Photocatalyst The visible light responsive photocatalyst according to the present invention used for the adsorption and oxidative decomposition of the volatile organic compound and / or the causative substance of bad odor or living odor is titanium dioxide (titanium oxide, TiO 2 ), zinc oxide (ZnO), cadmium sulfide (CdS) and tungsten oxide (WO 3 ). It is said that there is not much difference in the decomposition ability of each organic compound of these photocatalysts.
しかしながら、光触媒としての酸化チタンはその活性化のため、太陽光の中でもエネルギーが高い短波長光(紫外線等)が必要である。
また酸化亜鉛および硫化カドミウムの場合は、長期間の光吸収により触媒自身が分解し、有害な亜鉛イオンまたはカドミウムイオンを発生するので好ましくない。
However, because titanium oxide as a photocatalyst is activated, short-wavelength light (ultraviolet rays or the like) having high energy is necessary even in sunlight.
In the case of zinc oxide and cadmium sulfide, the catalyst itself is decomposed by light absorption over a long period of time, and harmful zinc ions or cadmium ions are generated.
そこで、本発明による可視光応答型光触媒−吸着剤複合体には、可視光応答型触媒として酸化タングステン(WO3)が好適に用いられる。しかしながら、本発明において用いられる酸化タングステンは化学式WO3を有する酸化タングステンに限定されず、化学式WO20O58、WO24O68またはWO25O73を有する酸化タングステンも用いることができ、少なくとも酸化タングステンを含む可視光の照射によって光触媒活性を示す可視光応答型の光触媒材料であればよい。 Therefore, tungsten oxide (WO 3 ) is suitably used as the visible light responsive catalyst in the visible light responsive photocatalyst-adsorbent complex according to the present invention. However, the tungsten oxide used in the present invention is not limited to tungsten oxide having the chemical formula WO 3, and tungsten oxide having the chemical formula WO 20 O 58 , WO 24 O 68 or WO 25 O 73 can be used, and at least tungsten oxide. Any visible light responsive photocatalytic material that exhibits photocatalytic activity when irradiated with visible light may be used.
本発明に用いられる酸化タングステン粒子の製造方法としては、パラタングステン酸アンモニウム(APT)を加熱分解する方法、金属タングステン粉末を酸素雰囲気中で加熱する方法等がある。得られる酸化タングステンの粒子径分布が大きい場合は、適当なフィルターを介して粒子径が大きい酸化タングステンを除去してもよい。 Examples of the method for producing tungsten oxide particles used in the present invention include a method of thermally decomposing ammonium paratungstate (APT), a method of heating metallic tungsten powder in an oxygen atmosphere, and the like. When the particle size distribution of the obtained tungsten oxide is large, the tungsten oxide having a large particle size may be removed through an appropriate filter.
酸化タングステン粒子は、粒子径の均一な粒子からなるものであっても、粒子径の不均一な粒子の混合物からなるものであってもよい。
しかしながら、酸化タングステンの一次粒子径は、5nm以上100nm以下であることが好ましい。
The tungsten oxide particles may be composed of particles having a uniform particle size or may be composed of a mixture of particles having a non-uniform particle size.
However, the primary particle diameter of tungsten oxide is preferably 5 nm or more and 100 nm or less.
酸化タンステンの一次粒子径が、5nmより小さいと凝集して2次粒子を形成し易くなり、100nmより大きいと比表面積が小さくなり、光触媒活性が低下する傾向にある。
なお、ここでいう粒子径とは、BET比表面積に基づいて算出された平均粒子径である。また、光触媒粒子の粒度分布の広がり(大きさ)および分布形状は特に限定されるものではなく、粒度分布のピークが複数存在してもよい。
When the primary particle diameter of the tantalum oxide is smaller than 5 nm, the particles tend to aggregate to form secondary particles. When the primary particle diameter is larger than 100 nm, the specific surface area decreases and the photocatalytic activity tends to decrease.
In addition, the particle diameter here is an average particle diameter calculated based on the BET specific surface area. Further, the spread (size) and distribution shape of the particle size distribution of the photocatalyst particles are not particularly limited, and a plurality of particle size distribution peaks may exist.
助触媒
助触媒は、電子吸引性を有する金属または金属化合物から構成され、光触媒の光触媒活性を高める目的で、本発明による可視光応答型光触媒−吸着剤複合体に添加できる。
前記助触媒としては、白金、金、銀、銅、パラジウム、鉄、ニッケル、ルテニウム、イリジウム、ニオブおよびモリブデン等の金属、ならびにそのハロゲン化物、酸化物、水酸化物または塩が挙げられる。
Cocatalyst The cocatalyst is composed of a metal or a metal compound having an electron-withdrawing property, and can be added to the visible light responsive photocatalyst-adsorbent complex according to the present invention for the purpose of enhancing the photocatalytic activity of the photocatalyst.
Examples of the promoter include metals such as platinum, gold, silver, copper, palladium, iron, nickel, ruthenium, iridium, niobium and molybdenum, and halides, oxides, hydroxides or salts thereof.
具体的には、白金、金、銀、銅、パラジウム、鉄、ニッケル、ルテニウム、イリジウム、ニオブおよびモリブデン等の金属、ならびにその塩化物、臭化物、ヨウ化物、酸化物、水酸化物、硫酸塩、硝酸塩、炭酸塩、リン酸塩、有機酸塩等が挙げられる。
助触媒の触媒能力及びコストの観点から、特に白金、パラジウムおよび銅、そのハロゲン化物、酸化物、水酸化物または塩が好ましい。
Specifically, metals such as platinum, gold, silver, copper, palladium, iron, nickel, ruthenium, iridium, niobium and molybdenum, and their chlorides, bromides, iodides, oxides, hydroxides, sulfates, Examples thereof include nitrates, carbonates, phosphates, and organic acid salts.
From the viewpoint of the catalytic ability and cost of the promoter, platinum, palladium and copper, halides, oxides, hydroxides or salts thereof are particularly preferable.
助触媒の添加方法
酸化タングステン粒子への助触媒の添加方法は:
(1)酸化タングステン粒子と、助触媒を構成する金属粒子または金属化合物粒子とを混練する方法;
(2)酸化タングステン粒子を、助触媒を構成する金属または金属化合物を含む溶液に添加した後、得られた溶液の加熱、あるいは得られた溶液に光照射して酸化タングステンの表面に、助触媒を構成する金属または金属化合物を析出させる方法;
等が挙げられる。
Cocatalyst addition method The cocatalyst addition method to the tungsten oxide particles is:
(1) A method of kneading tungsten oxide particles and metal particles or metal compound particles constituting a promoter;
(2) After adding tungsten oxide particles to a solution containing a metal or a metal compound constituting the promoter, the resulting solution is heated or irradiated with light to form a promoter on the surface of tungsten oxide. A method of depositing a metal or a metal compound constituting
Etc.
助触媒は、光触媒である酸化タングステンの重量に対して0.01〜3重量%の割合で添加するのが好ましい。
助触媒の添加量が酸化タングステンの重量に対して0.01重量%より少ないと、酸化タングステンの触媒作用において、助触媒としての効果が小さくなり高い光触媒活性が得られない。
また、助触媒の添加量が酸化タングステンの重量に対して3重量%より多いと、酸化タングステン表面における助触媒による表面被覆率が高くなり、酸化タングステンに届く光量が減少し、光触媒としての触媒作用が低下することがあり得るので好ましくない。
The cocatalyst is preferably added in a proportion of 0.01 to 3% by weight based on the weight of tungsten oxide as a photocatalyst.
When the added amount of the cocatalyst is less than 0.01% by weight with respect to the weight of tungsten oxide, the effect as a cocatalyst is reduced in the catalytic action of tungsten oxide, and high photocatalytic activity cannot be obtained.
Further, when the amount of the cocatalyst added is more than 3% by weight with respect to the weight of tungsten oxide, the surface coverage by the cocatalyst on the tungsten oxide surface increases, the amount of light reaching the tungsten oxide decreases, and the catalytic action as a photocatalyst. Is not preferred because it may decrease.
吸着剤
上記の化学物質を吸着し、分解する可視光応答型光触媒−吸着剤複合体を構成する吸着剤としては、ゼオライトの中でもハイシリカゼオライトが好適に用いられる。
上記のハイシリカゼオライトは、微粉末、粉末、ビーズまたはペレットのいずれの形状でも構わないが、本発明による可視光応答型光触媒−吸着剤複合体の、塗装、懸濁液の噴霧等への用途を考慮すると、粒径0.1〜20μmを有する粒子が好ましい。
Adsorbent As the adsorbent constituting the visible light responsive photocatalyst-adsorbent complex that adsorbs and decomposes the above chemical substances, high silica zeolite is preferably used among zeolites.
The above-mentioned high silica zeolite may be in the form of fine powder, powder, beads or pellets, but the application of the visible light responsive photocatalyst-adsorbent complex according to the present invention to coating, spraying of suspension, etc. In view of the above, particles having a particle size of 0.1 to 20 μm are preferable.
上記のハイシリカゼオライトは、化学物質の吸着能の観点から、陽イオンが、ナトリウムおよびカリウムよりも水素である水素型ハイシリカゼオライトが好ましく、その結晶形はこだわらないが、ベータ形またはZSM−5形が特に好ましい。
上記のハイシリカゼオライトは、化学物質の吸着能の観点からSiO2/Al2O3組成比が高いハイシリカゼオライトが好ましく、SiO2/Al2O3組成比1200〜2200を有するハイシリカゼオライトが特に好ましい。
The above-mentioned high silica zeolite is preferably a hydrogen type high silica zeolite whose cation is hydrogen rather than sodium and potassium from the viewpoint of the adsorption ability of chemical substances, and its crystal form is not particular, but the beta form or ZSM-5 The shape is particularly preferred.
The high silica zeolite is preferably a high silica zeolite having a high SiO 2 / Al 2 O 3 composition ratio from the viewpoint of the adsorption ability of chemical substances, and a high silica zeolite having a SiO 2 / Al 2 O 3 composition ratio of 1200 to 2200 is preferred. Particularly preferred.
一般的に、ゼオライトを構成するシリカ(Si)は周りに4個の酸素(O)をもつ構造をとり、正四面体構造を形成している。アルミナ(Al)は大きさがシリカと似ており、かわりにその位置に入ることがあるが、アルミナは3価のため、Al−という1価の負帯電の元素となる。結晶全体が中性を保つ必要があるため、プロトンH+がこの役割をするとブレーンステッド酸点となる。通常、これにより触媒活性となる。 In general, silica (Si) constituting zeolite has a structure having four oxygens (O) around it and forms a tetrahedral structure. Alumina (Al) is similar magnitude with silica, it is to enter its position instead, for alumina trivalent, Al - the monovalent negatively charged element called. Since it is necessary to keep the whole crystal neutral, when the proton H + plays this role, it becomes a Bransted acid point. This usually results in catalytic activity.
一方、アルデヒドの有するカルボニル酸素は、非共有電子対を持っているため、弱いルイス塩基の性質があり、ハイシリカゼオライトのプロトンH+に引き寄せられる。したがって、アルミナ比が高い、すなわちブレーンステッド酸点が多いハイシリカゼオライトはアルデヒドとの結合が強く、アルミナ比の低い、すなわちハイシリカゼオライトはアルデヒドとの結合が弱いということが考えられる。
アルデヒドとハイシリカゼオライトの結合力が弱ければ、一度ハイシリカゼオライトに吸着されたアルデヒドは簡単に光触媒で分解されやすく、本発明での所望の効果がえられたものと考えられる。
On the other hand, the carbonyl oxygen possessed by the aldehyde has a weak Lewis base property because it has an unshared electron pair, and is attracted to the proton H + of the high silica zeolite. Therefore, it is considered that the high silica zeolite having a high alumina ratio, that is, having a large number of brainsted acid points, has a strong bond with an aldehyde, and the low alumina ratio, that is, the high silica zeolite has a low bond with an aldehyde.
If the binding force between the aldehyde and the high silica zeolite is weak, the aldehyde once adsorbed on the high silica zeolite is easily decomposed by the photocatalyst, and it is considered that the desired effect in the present invention was obtained.
したがって、SiO2/Al2O3組成比が1200より低い場合、ハイシリカゼオライトと揮発性有機化合物のとの吸着力が強く、ハイシリカゼオライトの細孔内に吸着された化学物質がハイシリカゼオライト表面で光触媒により酸化分解を受け難くなっているものと考えられる。また、SiO2/Al2O3組成比が2200より高いハイシリカゼオライトは入手が容易ではない。
ハイシリカゼオライトは、揮発性有機化合物または悪臭の原因物質の吸着特性の観点から、細孔径5Å(0.5nm)以上7Å(0.7nm)未満を有するものが好ましい。
Therefore, when the SiO 2 / Al 2 O 3 composition ratio is lower than 1200, the adsorptive power between the high silica zeolite and the volatile organic compound is strong, and the chemical substance adsorbed in the pores of the high silica zeolite is the high silica zeolite. It is thought that the surface is less susceptible to oxidative degradation by the photocatalyst. Further, high silica zeolite having a SiO 2 / Al 2 O 3 composition ratio higher than 2200 is not easily available.
The high silica zeolite preferably has a pore diameter of 5 mm (0.5 nm) or more and less than 7 mm (0.7 nm) from the viewpoint of adsorption characteristics of a volatile organic compound or a odor-causing substance.
本発明による可視光応答型光触媒−吸着剤複合体におけるハイシリカゼオライトの添加量は、酸化タングステン粒子の重量に対して、10〜80重量%が好ましい。
ハイシリカゼオライトの添加量が、10重量%より低い場合にはハイシリカゼオライトによる吸着効果が低くなり、80重量%より高い場合にはハイシリカゼオライトに対する光触媒としての酸化タングステンの相対量が低くなり、十分な光触媒による酸化分解能が得られにくくなるものと思われる。
The addition amount of the high silica zeolite in the visible light responsive photocatalyst-adsorbent complex according to the present invention is preferably 10 to 80% by weight based on the weight of the tungsten oxide particles.
When the addition amount of the high silica zeolite is lower than 10% by weight, the adsorption effect by the high silica zeolite is low, and when it is higher than 80% by weight, the relative amount of tungsten oxide as a photocatalyst with respect to the high silica zeolite is low, It seems that it becomes difficult to obtain sufficient oxidation resolution by the photocatalyst.
光触媒複合体の製造方法
水を分散媒体とし、水に対する重量割合にして20%の酸化タングステン分散液に、酸化タングステンの重量に対して5〜25重量%となるようにハイシリカゼオライト粉末を添加し、撹拌混合してから乾燥・粉砕して光触媒複合体を作製する。
複合体の製造時には、予めハイシリカゼオライトを例えばビーズミルなどで粉砕してから光触媒と混合するか、あるいは光触媒とハイシリカゼオライトの混合時にビーズミルなどにて粉砕しながら混合してもよい。
Method for producing photocatalyst composite High silica zeolite powder is added to a tungsten oxide dispersion liquid in a weight ratio of 20% by weight with respect to the weight of water to 5 to 25% by weight with respect to the weight of tungsten oxide. Then, after stirring and mixing, drying and pulverization are performed to produce a photocatalyst complex.
In the production of the composite, the high silica zeolite may be pulverized in advance with a bead mill or the like and then mixed with the photocatalyst, or may be mixed while being pulverized with a bead mill or the like when the photocatalyst and the high silica zeolite are mixed.
あるいは、10重量%HSZ−891HOAハイシリカゼオライト懸濁液を予めビーズミル(日本コークス工業社製)にて30分、60分または90分間粉砕した粉砕ハイシリカゼオライト懸濁液を、酸化タングステンの重量に対して50重量%となるように、20%の酸化タングステン分散液に添加し、撹拌混合してから乾燥・粉砕して光触媒複合体を作製する。 Alternatively, a pulverized high silica zeolite suspension obtained by previously pulverizing a 10 wt% HSZ-891HOA high silica zeolite suspension with a bead mill (manufactured by Nippon Coke Kogyo Co., Ltd.) for 30 minutes, 60 minutes or 90 minutes is used as the weight of tungsten oxide. On the other hand, it is added to a 20% tungsten oxide dispersion so as to be 50% by weight, mixed with stirring, dried and pulverized to produce a photocatalyst complex.
以下、実施例および比較例により本発明を具体的に説明するが、これらの実施例により本発明が限定されるものではない。 EXAMPLES Hereinafter, although an Example and a comparative example demonstrate this invention concretely, this invention is not limited by these Examples.
実施例1
市販の粒子径(メジアン径:d50)45〜50μmの酸化タングステン(日本新金属社、99.9%)135gをイオン交換水1215g中に分散させた後、ビーズ径φ0.1mm(ニッカトー)を用いるビーズミル装置(日本コークス工業、MSC50)を用い、周速10m/s、粉砕、分散を360分間行い、メジアン径0.15〜0.20μmの酸化タングステン粒子の分散液を得た。
Example 1
After dispersing 135 g of tungsten oxide (Nippon Shin Metals Co., Ltd., 99.9%) having a particle diameter (median diameter: d50) of 45 to 50 μm in 1215 g of ion-exchanged water, a bead diameter of 0.1 mm (Nikkato) is used. Using a bead mill (Nippon Coke Industries, MSC50), the peripheral speed was 10 m / s, pulverization and dispersion were performed for 360 minutes to obtain a dispersion of tungsten oxide particles having a median diameter of 0.15 to 0.20 μm.
得られた酸化タングステン粒子の分散液に、酸化タングステン粒子の重量に対して、白金単体での重量の割合が0.025重量%となるように、ヘキサクロロ白金(VI)6水和物(キシダ化学、98.5%)の1%水溶液2.5部添加した。
その後、上記分散液を100℃で加熱して、水分を蒸発させた後、400℃で30分焼成することにより、0.025重量%の白金(助触媒)を担持させた酸化タングステン粒子を得た。
In the obtained dispersion of tungsten oxide particles, hexachloroplatinum (VI) hexahydrate (Kishida Chemical Co., Ltd.) was prepared so that the weight ratio of platinum alone to the weight of tungsten oxide particles was 0.025 wt%. , 98.5%) 2.5% of a 1% aqueous solution was added.
Thereafter, the dispersion is heated at 100 ° C. to evaporate water, and then calcined at 400 ° C. for 30 minutes to obtain tungsten oxide particles carrying 0.025% by weight of platinum (promoter). It was.
上記光触媒に固形分濃度が約20重量%となるよう水を添加し、得られた光触媒スラリー10gに、ハイシリカゼオライト混合割合が10重量%となるように市販のハイシリカゼオライト粉末(東ソー、HSZ−891HOA、SiO2/Al2O3比1,500、結晶形ZSM−5形)0.22gを加え、マグネチックスターラーにて1時間撹拌後、乾燥・粉砕して可視光応答型光触媒−吸着剤複合体を得た。 Water was added to the photocatalyst so as to have a solid content concentration of about 20% by weight, and commercially available high silica zeolite powder (Tosoh, HSZ) was added to 10 g of the obtained photocatalyst slurry so that the mixing ratio of high silica zeolite was 10% by weight. -891HOA, SiO 2 / Al 2 O 3 ratio 1,500, crystalline ZSM-5 form) 0.22 g, stirred with a magnetic stirrer for 1 hour, dried and ground, visible light responsive photocatalyst-adsorption An agent complex was obtained.
実施例2
実施例1において、ハイシリカゼオライト混合割合を30重量%となるように加えた以外は、実施例1と全く同様にして、可視光応答型光触媒−吸着剤複合体を得た。
Example 2
In Example 1, a visible light responsive photocatalyst-adsorbent complex was obtained in exactly the same manner as in Example 1, except that the mixing ratio of the high silica zeolite was 30% by weight.
実施例3
実施例1において、ハイシリカゼオライト混合割合が20重量%となるように市販のハイシリカゼオライト粉末(東ソー、HSZ−990HOA、SiO2/Al2O3比1,700、結晶形ベータ形)を用いた以外は、実施例1と全く同様にして、可視光応答型光触媒−吸着剤複合体を得た。
Example 3
In Example 1, a commercially available high silica zeolite powder (Tosoh, HSZ-990HOA, SiO 2 / Al 2 O 3 ratio 1,700, crystalline beta form) was used so that the mixing ratio of high silica zeolite was 20% by weight. A visible light responsive photocatalyst-adsorbent complex was obtained in the same manner as in Example 1 except that.
実施例4
市販のハイシリカゼオライト粉末(東ソー、HSZ−891HOA、SiO2/Al2O3比1,500、結晶形ZSM−5形)の10重量%水懸濁液を予めビーズミル(日本コークス工業社製)にて30分間粉砕し、この粉砕ハイシリカゼオライト懸濁液を、酸化タングステンの重量に対して50重量%となるように、20%の酸化タングステン分散液に添加し、撹拌混合してから乾燥・粉砕して可視光応答型光触媒−吸着剤複合体を得た。
Example 4
A bead mill (manufactured by Nihon Coke Kogyo Co., Ltd.) was prepared in advance with a 10% by weight aqueous suspension of commercially available high silica zeolite powder (Tosoh, HSZ-891HOA, SiO 2 / Al 2 O 3 ratio 1,500, crystalline ZSM-5 form). For 30 minutes, and add this pulverized high silica zeolite suspension to a 20% tungsten oxide dispersion so as to be 50% by weight with respect to the weight of tungsten oxide, and mix by stirring and drying. By grinding, a visible light responsive photocatalyst-adsorbent complex was obtained.
実施例5
実施例4において、粉砕ハイシリカゼオライト懸濁液の調製の際に、粉砕時間を60分間に変更した以外は、実施例4と全く同様にして、可視光応答型光触媒−吸着剤複合体を得た。
Example 5
In Example 4, a visible light responsive photocatalyst-adsorbent complex was obtained in exactly the same manner as in Example 4 except that the pulverization time was changed to 60 minutes when preparing the pulverized high silica zeolite suspension. It was.
実施例6
実施例4において、粉砕ハイシリカゼオライト懸濁液の調製の際に、粉砕時間を90分間に変更した以外は、実施例4と全く同様にして、可視光応答型光触媒−吸着剤複合体を得た。
Example 6
In Example 4, a visible light responsive photocatalyst-adsorbent complex was obtained in exactly the same manner as in Example 4 except that the pulverization time was changed to 90 minutes when preparing the pulverized high silica zeolite suspension. It was.
比較例1
実施例1において、ハイシリカゼオライト混合割合が10重量%となるように市販のハイシリカゼオライト粉末(東ソー、HSZ−390HUA、SiO2/Al2O3比500、結晶形Y形)を用いた以外は、実施例1と全く同様にして、可視光応答型光触媒−吸着剤複合体を得た。
Comparative Example 1
In Example 1, a commercially available high silica zeolite powder (Tosoh, HSZ-390HUA, SiO 2 / Al 2 O 3 ratio 500, crystal Y form) was used so that the mixing ratio of high silica zeolite was 10% by weight. In the same manner as in Example 1, a visible light responsive photocatalyst-adsorbent complex was obtained.
比較例2
実施例1において、ハイシリカゼオライト混合割合が40重量%となるように市販のハイシリカゼオライト粉末(東ソー、HSZ−860NHA、SiO2/Al2O3比70、結晶形ZSM−5形)を用いた以外は、実施例1と全く同様にして、可視光応答型光触媒−吸着剤複合体を得た。
Comparative Example 2
In Example 1, commercially available high silica zeolite powder (Tosoh, HSZ-860NHA, SiO 2 / Al 2 O 3 ratio 70, crystalline ZSM-5 form) was used so that the mixing ratio of high silica zeolite was 40% by weight. A visible light responsive photocatalyst-adsorbent complex was obtained in the same manner as in Example 1 except that.
比較例3
比較例2において、ハイシリカゼオライト混合割合が10重量%となるように加えた以外は、比較例2と全く同様にして、可視光応答型光触媒−吸着剤複合体を得た。
Comparative Example 3
A visible light responsive photocatalyst-adsorbent complex was obtained in the same manner as in Comparative Example 2, except that the mixing ratio of high silica zeolite in Comparative Example 2 was 10% by weight.
比較例4
実施例1において、ハイシリカゼオライトを用いないこと以外は、実施例1と全く同様にして、可視光応答型光触媒を得た。
Comparative Example 4
In Example 1, a visible light responsive photocatalyst was obtained in the same manner as in Example 1 except that high silica zeolite was not used.
比較例5
市販の二酸化チタン粉末(キシダ化学、99.5%)80gと尿素240gを混合し、400〜600℃で3時間焼成することで窒素ドープの酸化チタン粒子を可視光応答型光触媒として得た。
Comparative Example 5
80 g of commercially available titanium dioxide powder (Kishida Kagaku, 99.5%) and 240 g of urea were mixed and calcined at 400 to 600 ° C. for 3 hours to obtain nitrogen-doped titanium oxide particles as a visible light responsive photocatalyst.
比較例6
実施例4において、粉砕ハイシリカゼオライト懸濁液の調製の際に、粉砕時間を240分間に変更し、酸化タングステンを用いなかった以外は、実施例4と全く同様にして、可視光応答型光触媒を含まない吸着剤を得た。
なお、比較例6における吸着剤の調製の際に、粉砕時間を変更して得られたハイシリカゼオライトの粉砕時間に依存する結晶構造の変化を図5に示した。
Comparative Example 6
In Example 4, a visible light responsive photocatalyst was prepared in the same manner as in Example 4 except that, during the preparation of the pulverized high silica zeolite suspension, the pulverization time was changed to 240 minutes and tungsten oxide was not used. An adsorbent not containing was obtained.
In addition, the change of the crystal structure depending on the grinding time of the high silica zeolite obtained by changing the grinding time when preparing the adsorbent in Comparative Example 6 is shown in FIG.
以下の表1に実施例1〜6および比較例1〜6で得られた可視光応答型光触媒−吸着剤複合体および可視光応答型光触媒のそれぞれの特性を示す。 Table 1 below shows the respective characteristics of the visible light responsive photocatalyst-adsorbent complex and the visible light responsive photocatalyst obtained in Examples 1 to 6 and Comparative Examples 1 to 6.
実施例1〜6および比較例1〜6で得られた可視光応答型光触媒−吸着剤複合体、可視光応答型光触媒または吸着剤を用い、揮発性有機化合物の吸着・分解能の試験を、モデル化合物としてアセトアルデヒドを用いて行った。 Using the visible light responsive photocatalyst-adsorbent complex, the visible light responsive photocatalyst or the adsorbent obtained in Examples 1 to 6 and Comparative Examples 1 to 6, the adsorption / resolution tests of volatile organic compounds were modeled. Acetaldehyde was used as a compound.
可視光応答型光触媒−吸着剤複合体の評価照度
現在、事務所衛生基準規則では、精密な作業を行う場所では300Lx以上の照度、普通の作業を行う場所では100Lx以上の照度であることが規定されている。
また、通常、30W蛍光灯2灯を使用する八畳間では、300Lxの照度である。
さらに、晴れた日中、室内の南窓から約1mの室内の照度は、通常3,000〜5,000Lxであること等に基づき、本発明による可視光応答型光触媒−吸着剤複合体の以下の評価照度を500Lxおよび1,000Lxとした。
Evaluation illuminance of visible light responsive photocatalyst-adsorbent complex Currently, the office hygiene standard rules stipulate that the illuminance is 300Lx or more in a place where precise work is performed and the illuminance is 100Lx or more in a place where ordinary work is performed. Has been.
In addition, the illuminance is 300 Lx between the eight tatami mats using two 30 W fluorescent lamps.
Furthermore, the illuminance in the room approximately 1 m from the indoor south window during a sunny day is usually 3,000 to 5,000 Lx, etc., and the following of the visible light responsive photocatalyst-adsorbent complex according to the present invention is as follows. The evaluation illuminance was set to 500 Lx and 1,000 Lx.
可視光応答型光触媒−吸着剤複合体または可視光応答型光触媒によるアセトアルデヒドの酸化分解能(アセトアルデヒド残存率)
可視光応答型光触媒−吸着剤複合体または可視光応答型光触媒10mgをシャーレに入れ、そのシャーレを5Lのガスバッグに入れ、さらにアセトアルデヒドを300ppmの濃度となるように、そのガスバッグ内に導入した。
その後、そのガスバッグに対して白色LED(照度1000Lx)を照射し、アセトアルデヒドの残存量の経時変化および二酸化炭素の発生率をガス検知管で測定した。
以下の表に、白色LED(照度1000Lx)を照射下におけるアセトアルデヒドの残存率および二酸化炭素の発生率をそれぞれ示す。
Oxidation resolution of acetaldehyde by visible light responsive photocatalyst-adsorbent complex or visible light responsive photocatalyst (acetaldehyde residual rate)
A visible light responsive photocatalyst-adsorbent complex or 10 mg of a visible light responsive photocatalyst was placed in a petri dish, the petri dish was placed in a 5 L gas bag, and acetaldehyde was introduced into the gas bag to a concentration of 300 ppm. .
Then, white LED (illuminance 1000Lx) was irradiated with respect to the gas bag, and the time-dependent change of the residual amount of acetaldehyde and the generation rate of a carbon dioxide were measured with the gas detector tube.
The following tables show the residual rate of acetaldehyde and the generation rate of carbon dioxide under irradiation of a white LED (illuminance 1000 Lx), respectively.
二酸化炭素生成率=時間ごとの二酸化炭素量(ppm)/(アセトアルデヒド注入量(ppm)×2)
アセトアルデヒドは、炭素原子2個からなる化合物であるので、アセトアルデヒドが完全に酸化分解された際には、使用したアセトアルデヒドの2倍のモル濃度の二酸化炭素が理論上発生する。
Carbon dioxide production rate = carbon dioxide amount per hour (ppm) / (acetaldehyde injection amount (ppm) x 2)
Since acetaldehyde is a compound consisting of two carbon atoms, when acetaldehyde is completely oxidatively decomposed, carbon dioxide having a molar concentration twice that of the used acetaldehyde is theoretically generated.
上記の結果から、比較例5の二酸化チタンによるアセトアルデヒドの消失速度は、比較例4による酸化タングステン単体と同程度であったが、二酸化炭素の発生量が少ないことが判った。
これは、比較例5による二酸化チタンの場合、可視光線による二酸化チタンの活性化の度合いが紫外線より弱いため、アセトアルデヒドが完全に酸化分解されず、アセトアルデヒドの酸化分解反応過程で、中間体である酢酸、メタン、メタノール、ホルムアルデヒドまたはギ酸の段階で酸化分解反応が止まってしまうためと考えられる。
また、比較例6に示すようにハイシリカゼオライトをビーズミルで粉砕すると、結晶構造が破壊されることにより吸着性能が低下する。したがって、粉砕処理時間及びハイシリカゼオライトの添加量を適宜調整することにより光触媒複合体としての所望される特性を得ることができた。
From the above results, it was found that the disappearance rate of acetaldehyde by titanium dioxide of Comparative Example 5 was similar to that of the tungsten oxide simple substance of Comparative Example 4, but the amount of carbon dioxide generated was small.
This is because in the case of titanium dioxide according to Comparative Example 5, the activation of titanium dioxide by visible light is weaker than that of ultraviolet rays, so that acetaldehyde is not completely oxidatively decomposed, and acetic acid which is an intermediate in the process of oxidative decomposition of acetaldehyde. This is probably because the oxidative decomposition reaction stops at the methane, methanol, formaldehyde or formic acid stage.
In addition, as shown in Comparative Example 6, when high silica zeolite is pulverized with a bead mill, the adsorption performance is reduced due to the destruction of the crystal structure. Therefore, desired characteristics as a photocatalyst composite could be obtained by appropriately adjusting the grinding treatment time and the amount of high silica zeolite added.
可視光応答型光触媒−吸着剤複合体によるアセトアルデヒドの繰り返し分解能の加速試験評価
試験条件
実施例1によるHSZ−891HOAハイシリカゼオライト10重量%の可視光応答型光触媒−吸着剤複合体0.2gをシャーレに入れ、アセトアルデヒド30ppmが入った5Lのガスバックに入れ、白色LED(照度1000Lx)を照射し、24時間後のガスバックに存在するアセトアルデヒドの残存量から、可視光応答型光触媒−吸着剤複合体によるガスパック内におけるアセトアルデヒドの消臭率(%)を、初期の濃度(30ppm)に対し、消臭できた割合を消臭率として算出した。加速試験として、上記の使用したガスパックに24時間後に再びアセトアルデヒドを30ppmとなるように加え白色LED(照度1000Lx)を照射24時間後に消臭率を測定することを全15回行い、その結果を以下の表に示した。
Acceleration test evaluation test condition of repeated resolution of acetaldehyde by visible light responsive photocatalyst-adsorbent complex Test condition of 0.2 g of visible light responsive photocatalyst-adsorbent complex 10% by weight of HSZ-891HOA high silica zeolite according to Example 1 Into a 5 L gas bag containing 30 ppm acetaldehyde, irradiated with a white LED (illuminance 1000 Lx), and from the remaining amount of acetaldehyde present in the gas bag 24 hours later, a visible light responsive photocatalyst-adsorbent complex The deodorization rate (%) of acetaldehyde in the gas pack was calculated as the deodorization rate with respect to the initial concentration (30 ppm). As an acceleration test, acetaldehyde was added again to 30 ppm after 24 hours to the above used gas pack, and white LED (illuminance 1000 Lx) was irradiated and the deodorization rate was measured 24 hours later. It is shown in the following table.
上記の結果から、本発明による可視光応答型光触媒−吸着剤複合体は、30ppmのアセトアルデヒドを繰り返し加える加速試験を行っても、8回目迄はその90%以上を酸化分解することが分かり、本発明による可視光応答型光触媒−吸着剤複合体は通常の使用ではあり得ない程の過酷な試験でも十分にその効果を維持することが判った。 From the above results, it can be seen that the visible light responsive photocatalyst-adsorbent complex according to the present invention oxidatively decomposes 90% or more up to the 8th test even when an accelerated test in which 30 ppm of acetaldehyde is repeatedly added is performed. It has been found that the visible light responsive photocatalyst-adsorbent complex according to the invention can maintain its effect sufficiently even in such a severe test that it cannot be used normally.
本発明の可視光応答型光触媒−吸着剤複合体は、揮発性有機化合物の、高い吸着能力、および可視光応答型光触媒による高い分解能力を有するので、壁紙、壁紙用接着剤、壁用塗料、カーペット、フィルター等に添加して長期間に亘り使用できる。また容器に入れて、室内において脱臭剤として提供され得る。 Since the visible light responsive photocatalyst-adsorbent complex of the present invention has a high adsorption ability of a volatile organic compound and a high decomposition ability by a visible light responsive photocatalyst, wallpaper, wallpaper adhesive, wall paint, Can be used for a long time by adding to carpets, filters, etc. It can also be provided in a container as a deodorant indoors.
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