JPH0975747A - Method for caking photocatalyst - Google Patents
Method for caking photocatalystInfo
- Publication number
- JPH0975747A JPH0975747A JP25815595A JP25815595A JPH0975747A JP H0975747 A JPH0975747 A JP H0975747A JP 25815595 A JP25815595 A JP 25815595A JP 25815595 A JP25815595 A JP 25815595A JP H0975747 A JPH0975747 A JP H0975747A
- Authority
- JP
- Japan
- Prior art keywords
- photocatalyst
- lime
- agent
- alumina
- silica
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000011941 photocatalyst Substances 0.000 title claims abstract description 64
- 238000000034 method Methods 0.000 title claims description 12
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 40
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 39
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims abstract description 26
- 235000011941 Tilia x europaea Nutrition 0.000 claims abstract description 26
- 239000004571 lime Substances 0.000 claims abstract description 26
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract description 23
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000000377 silicon dioxide Substances 0.000 claims abstract description 18
- NDVLTYZPCACLMA-UHFFFAOYSA-N silver oxide Chemical compound [O-2].[Ag+].[Ag+] NDVLTYZPCACLMA-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000000203 mixture Substances 0.000 claims abstract description 16
- 239000004568 cement Substances 0.000 claims abstract description 15
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims abstract description 11
- 230000036571 hydration Effects 0.000 claims abstract description 11
- 238000006703 hydration reaction Methods 0.000 claims abstract description 11
- 229910001923 silver oxide Inorganic materials 0.000 claims abstract description 9
- 239000000654 additive Substances 0.000 claims abstract description 6
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 claims abstract description 6
- 230000000996 additive effect Effects 0.000 claims abstract description 5
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 51
- 239000000292 calcium oxide Substances 0.000 claims description 26
- 235000012255 calcium oxide Nutrition 0.000 claims description 26
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 claims description 4
- 238000002156 mixing Methods 0.000 claims description 3
- 239000003607 modifier Substances 0.000 claims description 3
- 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 1
- 229910001930 tungsten oxide Inorganic materials 0.000 claims 1
- 239000011787 zinc oxide Substances 0.000 claims 1
- 239000000463 material Substances 0.000 abstract description 5
- 230000001105 regulatory effect Effects 0.000 abstract 1
- 238000006243 chemical reaction Methods 0.000 description 22
- 238000007711 solidification Methods 0.000 description 11
- 230000008023 solidification Effects 0.000 description 11
- 239000000126 substance Substances 0.000 description 11
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 8
- 239000000843 powder Substances 0.000 description 8
- 239000010802 sludge Substances 0.000 description 8
- XFWJKVMFIVXPKK-UHFFFAOYSA-N calcium;oxido(oxo)alumane Chemical compound [Ca+2].[O-][Al]=O.[O-][Al]=O XFWJKVMFIVXPKK-UHFFFAOYSA-N 0.000 description 7
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 6
- 239000000378 calcium silicate Substances 0.000 description 6
- 229910052918 calcium silicate Inorganic materials 0.000 description 6
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 description 6
- 150000003839 salts Chemical class 0.000 description 6
- 238000004056 waste incineration Methods 0.000 description 6
- 239000002699 waste material Substances 0.000 description 5
- 230000009931 harmful effect Effects 0.000 description 4
- 239000002440 industrial waste Substances 0.000 description 4
- SQGYOTSLMSWVJD-UHFFFAOYSA-N silver(1+) nitrate Chemical compound [Ag+].[O-]N(=O)=O SQGYOTSLMSWVJD-UHFFFAOYSA-N 0.000 description 4
- 238000005245 sintering Methods 0.000 description 4
- -1 sodium hydroxycitrate citrate Chemical compound 0.000 description 4
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 3
- WMFOQBRAJBCJND-UHFFFAOYSA-M Lithium hydroxide Chemical compound [Li+].[OH-] WMFOQBRAJBCJND-UHFFFAOYSA-M 0.000 description 3
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 3
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- DNIAPMSPPWPWGF-UHFFFAOYSA-N Propylene glycol Chemical compound CC(O)CO DNIAPMSPPWPWGF-UHFFFAOYSA-N 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 239000007864 aqueous solution Substances 0.000 description 3
- 230000003197 catalytic effect Effects 0.000 description 3
- 238000000354 decomposition reaction Methods 0.000 description 3
- 238000009472 formulation Methods 0.000 description 3
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 230000001954 sterilising effect Effects 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 description 2
- 229920001732 Lignosulfonate Polymers 0.000 description 2
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 2
- 239000011398 Portland cement Substances 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- 239000002250 absorbent Substances 0.000 description 2
- 230000002745 absorbent Effects 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 229940043430 calcium compound Drugs 0.000 description 2
- 150000001674 calcium compounds Chemical class 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 235000011116 calcium hydroxide Nutrition 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 238000006482 condensation reaction Methods 0.000 description 2
- 238000007596 consolidation process Methods 0.000 description 2
- 229920001577 copolymer Polymers 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000004088 foaming agent Substances 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 238000000465 moulding Methods 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 229910001961 silver nitrate Inorganic materials 0.000 description 2
- 238000004659 sterilization and disinfection Methods 0.000 description 2
- UOCLXMDMGBRAIB-UHFFFAOYSA-N 1,1,1-trichloroethane Chemical compound CC(Cl)(Cl)Cl UOCLXMDMGBRAIB-UHFFFAOYSA-N 0.000 description 1
- AEQDJSLRWYMAQI-UHFFFAOYSA-N 2,3,9,10-tetramethoxy-6,8,13,13a-tetrahydro-5H-isoquinolino[2,1-b]isoquinoline Chemical compound C1CN2CC(C(=C(OC)C=C3)OC)=C3CC2C2=C1C=C(OC)C(OC)=C2 AEQDJSLRWYMAQI-UHFFFAOYSA-N 0.000 description 1
- CYDQOEWLBCCFJZ-UHFFFAOYSA-N 4-(4-fluorophenyl)oxane-4-carboxylic acid Chemical compound C=1C=C(F)C=CC=1C1(C(=O)O)CCOCC1 CYDQOEWLBCCFJZ-UHFFFAOYSA-N 0.000 description 1
- 101710134784 Agnoprotein Proteins 0.000 description 1
- 239000003109 Disodium ethylene diamine tetraacetate Substances 0.000 description 1
- OVBJJZOQPCKUOR-UHFFFAOYSA-L EDTA disodium salt dihydrate Chemical compound O.O.[Na+].[Na+].[O-]C(=O)C[NH+](CC([O-])=O)CC[NH+](CC([O-])=O)CC([O-])=O OVBJJZOQPCKUOR-UHFFFAOYSA-L 0.000 description 1
- KIWBPDUYBMNFTB-UHFFFAOYSA-N Ethyl hydrogen sulfate Chemical compound CCOS(O)(=O)=O KIWBPDUYBMNFTB-UHFFFAOYSA-N 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- QIMAVGCKUQHCOL-UHFFFAOYSA-L O=C(CC(C(=O)[O-])=O)C(=O)[O-].[Na+].[Na+] Chemical compound O=C(CC(C(=O)[O-])=O)C(=O)[O-].[Na+].[Na+] QIMAVGCKUQHCOL-UHFFFAOYSA-L 0.000 description 1
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 description 1
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- 229920002125 Sokalan® Polymers 0.000 description 1
- 229910010413 TiO 2 Inorganic materials 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 150000008043 acidic salts Chemical class 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 150000008051 alkyl sulfates Chemical class 0.000 description 1
- 229940037003 alum Drugs 0.000 description 1
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000001934 delay Effects 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 235000019301 disodium ethylene diamine tetraacetate Nutrition 0.000 description 1
- 239000000839 emulsion Substances 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000000499 gel Substances 0.000 description 1
- 235000011187 glycerol Nutrition 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 239000003456 ion exchange resin Substances 0.000 description 1
- 229920003303 ion-exchange polymer Polymers 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 235000019341 magnesium sulphate Nutrition 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 239000010446 mirabilite Substances 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- PSZYNBSKGUBXEH-UHFFFAOYSA-M naphthalene-1-sulfonate Chemical compound C1=CC=C2C(S(=O)(=O)[O-])=CC=CC2=C1 PSZYNBSKGUBXEH-UHFFFAOYSA-M 0.000 description 1
- 229930014626 natural product Natural products 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- WXZMFSXDPGVJKK-UHFFFAOYSA-N pentaerythritol Chemical compound OCC(CO)(CO)CO WXZMFSXDPGVJKK-UHFFFAOYSA-N 0.000 description 1
- 230000001699 photocatalysis Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000004584 polyacrylic acid Substances 0.000 description 1
- 235000011118 potassium hydroxide Nutrition 0.000 description 1
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical compound [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 description 1
- 229910052939 potassium sulfate Inorganic materials 0.000 description 1
- 235000011151 potassium sulphates Nutrition 0.000 description 1
- AVTYONGGKAJVTE-UHFFFAOYSA-L potassium tartrate Chemical compound [K+].[K+].[O-]C(=O)C(O)C(O)C([O-])=O AVTYONGGKAJVTE-UHFFFAOYSA-L 0.000 description 1
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 description 1
- 235000012239 silicon dioxide Nutrition 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 239000000176 sodium gluconate Substances 0.000 description 1
- 235000012207 sodium gluconate Nutrition 0.000 description 1
- 229940005574 sodium gluconate Drugs 0.000 description 1
- 235000011121 sodium hydroxide Nutrition 0.000 description 1
- 239000001540 sodium lactate Substances 0.000 description 1
- 235000011088 sodium lactate Nutrition 0.000 description 1
- 229940005581 sodium lactate Drugs 0.000 description 1
- 239000001488 sodium phosphate Substances 0.000 description 1
- 229910000162 sodium phosphate Inorganic materials 0.000 description 1
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 description 1
- 229940074404 sodium succinate Drugs 0.000 description 1
- ZDQYSKICYIVCPN-UHFFFAOYSA-L sodium succinate (anhydrous) Chemical compound [Na+].[Na+].[O-]C(=O)CCC([O-])=O ZDQYSKICYIVCPN-UHFFFAOYSA-L 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 150000005846 sugar alcohols Polymers 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 230000008961 swelling Effects 0.000 description 1
- RYFMWSXOAZQYPI-UHFFFAOYSA-K trisodium phosphate Chemical compound [Na+].[Na+].[Na+].[O-]P([O-])([O-])=O RYFMWSXOAZQYPI-UHFFFAOYSA-K 0.000 description 1
- WFKWXMTUELFFGS-UHFFFAOYSA-N tungsten Chemical compound [W] WFKWXMTUELFFGS-UHFFFAOYSA-N 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 239000010937 tungsten Substances 0.000 description 1
- ZNOKGRXACCSDPY-UHFFFAOYSA-N tungsten trioxide Chemical compound O=[W](=O)=O ZNOKGRXACCSDPY-UHFFFAOYSA-N 0.000 description 1
- 239000011882 ultra-fine particle Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 239000004563 wettable powder Substances 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Curing Cements, Concrete, And Artificial Stone (AREA)
- Catalysts (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】この発明は、酸化チタン、酸
化銀等の光触媒の固結方法に関するものであり、特に、
活性汚泥の焼却灰、都市ごみの焼却灰、産業廃棄物の焼
却灰等の廃棄物の焼却灰を利用した光触媒の固結方法に
関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for solidifying a photocatalyst such as titanium oxide or silver oxide.
The present invention relates to a method for consolidating a photocatalyst using incineration ash of activated sludge, incineration ash of municipal waste, incineration ash of industrial waste, and the like.
【0002】[0002]
【従来の技術】酸化チタン(TiO2)、酸化銀(Ag
O,Ag2O)等からなる光触媒に光を照射すると、強
力な酸化力を生じ、殺菌、悪臭分解、オゾン分解等の作
用を有することから、近年、例えばタイルやレンガ等の
建材に応用して、空気の清浄化、廃水中のオゾン処理、
病院内における殺菌等に利用することが提案されてい
る。ところで、上記酸化チタンや酸化銀は、通常粉末で
あるため、これにシリカ(SiO2 )やアルミナ(Al
2O3)等を添加し、高温で焼結固化することが行われて
いる。 2. Description of the Related Art Titanium oxide (TiO 2 ) and silver oxide (Ag
When a photocatalyst composed of O, Ag 2 O) or the like is irradiated with light, it has a strong oxidizing power, and has the effects of sterilization, foul odor decomposition, ozone decomposition, etc. Therefore, it has recently been applied to building materials such as tiles and bricks. Clean air, treat ozone in wastewater,
It is proposed to use it for sterilization in hospitals. By the way, since the above-mentioned titanium oxide and silver oxide are usually powders, silica (SiO 2 ) and alumina (Al
2 O 3 ) and the like are added, and sintering and solidification are performed at high temperature.
【0003】[0003]
【発明が解決しようとする課題】しかし、酸化チタンは
高温で焼結すると、約600℃〜700℃の間でその結
晶構造がアナターゼ型からルチル型に変化し、その結
果、触媒活性が低下するといった問題が生じる。また、
高温で焼結するためには、多大な燃料が必要であり、コ
スト高を招来するものである。However, when titanium oxide is sintered at a high temperature, its crystal structure changes from anatase type to rutile type between about 600 ° C. and 700 ° C., and as a result, the catalytic activity decreases. Such a problem occurs. Also,
A large amount of fuel is required to sinter at a high temperature, resulting in high cost.
【0004】本発明は、上記問題点に鑑みなされたもの
であり、常温で速やかに光触媒の固結生成物を製造する
ことができる、光触媒の固結方法を実現することを目的
とするものである。The present invention has been made in view of the above problems, and an object of the present invention is to realize a method for consolidating a photocatalyst capable of rapidly producing a condensate product of the photocatalyst at room temperature. is there.
【0005】また、活性汚泥の焼却灰、都市ごみの焼却
灰、産業廃棄物の焼却灰等の廃棄物の焼却灰を利用し、
高温で焼結することなく常温で光触媒の固結生成物を製
造することができる、光触媒の固結方法の実現を目的と
するものである。Further, waste incineration ash such as activated sludge incineration ash, municipal solid waste incineration ash, industrial waste incineration ash, etc. is used,
It is an object of the present invention to realize a photocatalyst consolidation method capable of producing a photocatalyst consolidation product at room temperature without sintering at high temperature.
【0006】[0006]
【課題を解決するための手段】本発明は、シリカ(Si
O2 )やアルミナ(Al2O3)と、生石灰とを反応させ
て安定なカルシウム化合物(珪酸カルシウム、カルシウ
ムアルミネート)の硬化物を得る、いわゆるポゾラン反
応を利用して光触媒を固結しようとするものである。The present invention relates to silica (Si
O 2 ) or alumina (Al 2 O 3 ) is reacted with quick lime to obtain a stable hardened product of a calcium compound (calcium silicate, calcium aluminate), that is, so-called pozzolanic reaction is used to consolidate the photocatalyst. To do.
【0007】また、ポゾラン反応に不可欠なシリカ(S
iO2 )やアルミナ(Al2O3)が、活性汚泥の焼却
灰、都市ごみの焼却灰、産業廃棄物の焼却灰等に含有さ
れていることが多いことに着目し、ポゾラン反応を利用
してこれら焼却灰を光触媒の固結生成物として再資源化
しようとするものである。Further, silica (S which is indispensable for the pozzolanic reaction
Focusing on the fact that iO 2 ) and alumina (Al 2 O 3 ) are often contained in incinerated ash of activated sludge, incinerated ash of municipal waste, incinerated ash of industrial waste, etc., the pozzolanic reaction is used. The incinerated ash is to be recycled as a solidified product of the photocatalyst.
【0008】ところで、上記ポゾラン反応は、生石灰の
水に対する溶解度が 0.131(10℃)と極めて小さく、そ
の反応効率が低いため、反応を開始させる際に生石灰の
水に対する溶解度を高める石灰過飽和剤を添加すること
が必要である。By the way, in the pozzolanic reaction, the solubility of quicklime in water is extremely small at 0.131 (10 ° C.), and its reaction efficiency is low. Therefore, when starting the reaction, a lime supersaturating agent for increasing the solubility of quicklime in water is added. It is necessary to.
【0009】すなわち、本発明の光触媒の固結方法は、
光触媒に、シリカ、アルミナの少なくとも1種と、生石
灰及びセメント混合物を含有する固結剤と、石灰過飽和
材を含有する水和調節剤を主成分とする添加剤と、水と
を加えて混合し、硬化させるものである。That is, the method for consolidating a photocatalyst of the present invention is
To the photocatalyst, at least one of silica and alumina, a solidifying agent containing quicklime and a cement mixture, an additive containing a hydration regulator containing a lime supersaturated material as a main component, and water are added and mixed. , To cure.
【0010】また、光触媒に、シリカ、アルミナの少な
くとも1種を含有する焼却灰と、生石灰及びセメント混
合物を含有する固結剤と、石灰過飽和材を含有する水和
調節剤を主成分とする添加剤と、水とを加えて混合し、
硬化させることにより、廃棄物の焼却灰を光触媒の固結
生成物とするものである。Further, addition to the photocatalyst of which main components are incinerated ash containing at least one of silica and alumina, a solidifying agent containing quick lime and a cement mixture, and a hydration modifier containing a lime supersaturated material. Add the agent and water and mix,
By curing, the incineration ash of the waste is used as a solidification product of the photocatalyst.
【0011】本発明の光触媒としては、例えば酸化チタ
ン(TiO2 )、酸化銀(AgO,Ag2 O)、酸化亜
鉛(ZnO)、酸化タングステン(WO3 )のいずれか
が挙げられる。Examples of the photocatalyst of the present invention include titanium oxide (TiO 2 ), silver oxide (AgO, Ag 2 O), zinc oxide (ZnO), and tungsten oxide (WO 3 ).
【0012】光触媒に加えられたシリカ、アルミナと固
結剤中の生石灰とがポゾロン反応により固結を開始す
る。そして、石灰過飽和剤によりその反応効率が高めら
れ、固結反応が急激に進行するが、光触媒が存在するこ
とで上記石灰過飽和剤による急激な凝結進行は制御さ
れ、光触媒の粉末と、シリカ、アルミナ若しくはシリカ
又はアルミナを含む焼却灰と生石灰とが充分混合された
後に凝結反応が進行し、常温で光触媒の固結生成物が得
られる。Silica and alumina added to the photocatalyst and quicklime in the solidifying agent start solidification by a pozzolon reaction. Then, the reaction efficiency is increased by the lime supersaturating agent, and the solidification reaction rapidly progresses, but the rapid progress of condensation by the lime supersaturating agent is controlled by the presence of the photocatalyst, and the photocatalyst powder, silica, and alumina. Alternatively, after the incinerated ash containing silica or alumina and the quick lime are sufficiently mixed, the condensation reaction proceeds, and the solidified product of the photocatalyst is obtained at room temperature.
【0013】[0013]
【発明の実施の形態】以下に、本発明に係る光触媒の固
結方法を、廃棄物の焼却灰から光触媒の固結生成物を製
造する場合を例に挙げて具体的に説明する。固結対象の
光触媒は、通常粉末の酸化チタン(TiO2 )や酸化銀
(AgO,Ag2O )が挙げられるが、必ずしもこれに
限定されず、他の光触媒、例えば酸化亜鉛(ZnO)や
酸化タングステン(WO3 )にも適用可能である。BEST MODE FOR CARRYING OUT THE INVENTION The method for consolidating a photocatalyst according to the present invention will be specifically described below by taking as an example a case where a photocatalyst consolidating product is produced from waste incineration ash. Examples of the photocatalyst to be consolidated include usually titanium oxide (TiO 2 ) and silver oxide (AgO, Ag 2 O) which are powders, but the photocatalyst is not limited to this, and other photocatalysts such as zinc oxide (ZnO) and oxides. It is also applicable to tungsten (WO 3 ).
【0014】上記光触媒に加えられる焼却灰の種類は、
特に限定されるものではないが、ポゾラン反応を利用し
て光触媒を固結するものであることから、生石灰と反応
してカルシウム化合物(珪酸カルシウム、カルシウムア
ルミネート)の硬化物を得るため、シリカ(Si
O2 )、アルミナ(Al2O3)の少なくとも1種以上を
含有していることが必要である。即ち、シリカ(SiO
2 )、アルミナ(Al2O3)の少なくとも1種以上を含
有していれば、活性汚泥焼却灰、都市ごみ焼却灰、EP
灰(電気集塵機で集めたダストの焼却灰)、産業廃棄物
焼却灰等あらゆる種類の焼却灰が利用可能である。The types of incineration ash added to the above photocatalyst are
Although it is not particularly limited, since the photocatalyst is solidified by utilizing the pozzolanic reaction, silica (calcium silicate, calcium aluminate) is used to obtain a cured product of calcium compound (calcium silicate, calcium aluminate) by reacting with quicklime. Si
It is necessary to contain at least one of O 2 ) and alumina (Al 2 O 3 ). That is, silica (SiO
2 ) and alumina (Al 2 O 3 ) containing at least one kind, activated sludge incineration ash, municipal waste incineration ash, EP
All kinds of incineration ash such as ash (incineration ash of dust collected by an electric dust collector), industrial waste incineration ash can be used.
【0015】尚、焼却灰中には、固結反応の促進化ある
いは遅延化をもたらしたり、固結反応終了後に変化を与
える物質が含まれている可能性があることから、本発明
の実施前に予め使用する焼却灰の成分を分析し、弊害を
引き起こす物質の除去操作や安定化操作を前処理として
行うことが望ましい。例えば、鉄は固結後の酸化反応に
よって膨張し、固結生成物にクラックを生じさせる可能
性があるので、予め除鉄し、また、金属アルミニウムは
発泡して固結生成物の強度を劣化させるので、消石灰で
処理しカルシウムアルミネートとして安定化する。Since the incinerated ash may contain a substance that promotes or delays the solidification reaction or changes after the completion of the solidification reaction, before the present invention is carried out. It is desirable to analyze the components of the incineration ash used in advance in order to remove substances that cause harmful effects and to perform stabilization operations as pretreatment. For example, iron expands due to the oxidation reaction after solidification and may cause cracks in the solidified product, so iron is removed in advance, and metallic aluminum foams and deteriorates the strength of the solidified product. Therefore, it is treated with slaked lime and stabilized as calcium aluminate.
【0016】次に、本発明の固結剤は、生石灰95〜5
0%と、セメント5〜50%とを混合したものである。
セメントは、ポルトランドセメント、高炉スラグ、アル
ミナセメント、焼きミョウバン石、硅酸塩などの単独
物、あるいはこれらの中の2種以上の混合物である。本
発明において、焼却灰中のシリカやアルミナと固結剤と
が反応して得られる生成物は、硅酸カルシウムとカルシ
ウムアルミネートであることから、上記ポルトランドセ
メント水和物と同様のものが生成するのであるが、反応
初期に生成した硅酸カルシウム及びカルシウムアルミネ
ートは、非晶質のゲル状であり、強度が不足しているも
のである。そこで、ゲル状物質から結晶質の硅酸カルシ
ウム水和物やカルシウムアルミネートを生成しやすくす
るため、上記セメント類を添加して結晶の核とし、硬化
物の強度を高め耐水性も改善するのである。Next, the solidifying agent of the present invention is quicklime 95-5.
It is a mixture of 0% and 5 to 50% cement.
The cement is a single substance such as Portland cement, blast furnace slag, alumina cement, burnt alum, silicate, etc., or a mixture of two or more thereof. In the present invention, the product obtained by reacting the silica or alumina in the incinerated ash with the solidifying agent is calcium silicate and calcium aluminate, so that the same product as the above Portland cement hydrate is produced. However, the calcium silicate and calcium aluminate formed in the initial stage of the reaction are amorphous gels and lack strength. Therefore, in order to easily generate crystalline calcium silicate hydrate or calcium aluminate from a gel-like substance, the above cements are added to form the nucleus of the crystal, which increases the strength of the cured product and also improves the water resistance. is there.
【0017】また本発明の石灰過飽和剤は、生石灰の水
和時に作用して超微粒子の活性消石灰(コロイド状)の
生成と同時に生石灰の水に対する溶解度を高めて石灰の
過飽和状態を生じさせるための添加剤である。この石灰
過飽和剤として、例えば、ヒドロキシカルボン酸塩のク
エン酸ナトリウム、酒石酸カリウム、ケトカルボン酸塩
の2ケトグルタール酸ナトリウム、グルコン酸ナトリウ
ム、ジカルボン酸塩のEDTA2ナトリウム、コハク酸
ナトリウム、乳酸ナトリウム、天然物のフミン酸ナトリ
ウム、糖類、リグニンスルホン酸塩等が望ましい。ま
た、多価アルコール類のグリセリン、プロピレングリコ
ール、エチレングリコール、ペンタエリスリトールの単
体もしくはこれらの重合物もしくはこれらの共重合物、
ポリカルボン酸塩のポリアクリル酸塩、イソブチレン無
水マイレン酸共重合体塩等であってもよい。これらの石
灰過飽和剤は、粉末又は水溶液として使用され、単体又
はこれらのうちの2種以上を併用してもよい。The lime supersaturating agent of the present invention acts at the time of hydration of quick lime to form ultrafine particles of active slaked lime (colloidal form) and at the same time enhances the solubility of quick lime in water to cause a supersaturated state of lime. It is an additive. Examples of the lime supersaturating agent include sodium hydroxycitrate citrate, potassium tartarate, ketocarboxylate sodium diketoglutarate, sodium gluconate, dicarboxylate disodium EDTA, sodium succinate, sodium lactate, and natural products. Sodium humate, sugar, lignin sulfonate and the like are preferable. Further, polyhydric alcohols such as glycerin, propylene glycol, ethylene glycol, pentaerythritol alone or a polymer thereof or a copolymer thereof,
It may be a polyacrylic acid salt of a polycarboxylic acid salt, an isobutylene maleic anhydride copolymer salt, or the like. These lime supersaturants are used as a powder or an aqueous solution, and may be used alone or in combination of two or more thereof.
【0018】上記石灰過飽和剤を用いると、まず水溶液
中において石灰過飽和剤が生石灰と反応して錯塩を生
じ、次にこの錯塩が焼却灰と反応する。さらにその反応
後、石灰過飽和剤が遊離して再度生石灰と反応し、この
反応が繰り返し続くものである。従って、この石灰過飽
和剤は、少量でも十分な効果を発揮するものである。
尚、この石灰過飽和剤は、生石灰の水和遅延剤である、
苛性ソーダ、苛性カリ、水酸化リチウム、ケイフッ化マ
グネシウム、セスキケイ酸ソーダ等のアルカリ類と共に
共用することもできる。When the lime supersaturating agent is used, the lime supersaturating agent first reacts with quick lime in an aqueous solution to form a complex salt, and then the complex salt reacts with incineration ash. Further, after the reaction, the lime supersaturating agent is released and again reacts with quick lime, and this reaction continues repeatedly. Therefore, this lime supersaturating agent exerts a sufficient effect even in a small amount.
The lime supersaturating agent is a quick lime hydration retarder,
It can also be used together with alkalis such as caustic soda, caustic potash, lithium hydroxide, magnesium silicofluoride and sodium sesquisilicate.
【0019】上記石灰過飽和剤を含む水溶液は、生石灰
の水和が極めて遅くなるため、石灰過飽和剤が焼却灰に
吸収され、固液反応が生じる。その結果、焼却灰と生石
灰との反応が急激に効率的となり、焼却灰及び生石灰が
充分混合する前に、凝結反応が進行する急結現象が発生
するが、光触媒が存在していると、この急結現象は防止
され、光触媒の粉末、焼却灰及び生石灰が充分混合され
た後に凝結反応が進行する。In the aqueous solution containing the lime supersaturating agent, quick lime hydrates very slowly, so that the lime supersaturating agent is absorbed by the incineration ash and a solid-liquid reaction occurs. As a result, the reaction between the incineration ash and the quick lime becomes drastically efficient, and before the incineration ash and the quick lime are sufficiently mixed, a quick-setting phenomenon occurs in which the condensation reaction proceeds, but when the photocatalyst is present, The quick setting phenomenon is prevented, and the setting reaction proceeds after the photocatalyst powder, incineration ash and quick lime are thoroughly mixed.
【0020】尚、上記の通り、光触媒により急結現象は
防止されるが、硬化時間を調節するために、硬化遅延剤
を添加してもよい。この硬化遅延剤としては、例えば、
石膏、芒硝、硫酸カリウム、硫酸アルミニウム、硫酸マ
グネシウムもしくはこれらの酸性塩等が望ましく、また
硫酸エチルなどのアルキル硫酸、ナフタリンスルホン酸
塩、リグニンスルホン酸塩、有機アミンの硫酸塩等の有
機塩類も好適である。斯かる硫酸塩は、石灰過飽和剤と
組み合わせて使用すると、生石灰の水和速度と、光触媒
及び焼却灰の固化反応速度を遅延させることができ、該
硬化遅延剤の添加量を調節することにより、硬化時間を
おおむね5〜360分の間で自由に設定できるため、硬
化時間の異なるあらゆる成型方法、成型機械に対して対
応可能となる。As described above, the photocatalyst prevents the rapid setting phenomenon, but a curing retarder may be added to control the curing time. As the curing retarder, for example,
Gypsum, mirabilite, potassium sulfate, aluminum sulfate, magnesium sulfate, or an acidic salt thereof is preferable, and alkyl sulfates such as ethyl sulfate, organic salts such as naphthalene sulfonate, lignin sulfonate, and sulfate of organic amine are also preferable. Is. When such a sulfate is used in combination with a lime supersaturating agent, it is possible to delay the hydration rate of quicklime and the solidification reaction rate of photocatalyst and incineration ash, and by adjusting the addition amount of the hardening retarder, Since the curing time can be freely set to about 5 to 360 minutes, it can be applied to any molding method or molding machine having a different curing time.
【0021】また、硬化遅延剤を用いて硬化時間を調節
することにより、生石灰とセメントの混合物である固結
剤と、光触媒と、焼却灰とを均質に混合でき、均一なス
ラリーを得ることができる。Further, by adjusting the curing time using a curing retarder, the solidifying agent which is a mixture of quick lime and cement, the photocatalyst and the incineration ash can be homogeneously mixed to obtain a uniform slurry. it can.
【0022】上記の光触媒、固結剤、石灰過飽和剤、水
の配合量は、焼却灰100重量部当たり、光触媒1重量
部〜10重量部、好ましくは3重量部〜7重量部、固結
剤10重量部〜70重量部、好ましくは20重量部〜6
0重量部、石灰過飽和剤0.01重量部〜5重量部、好
ましくは0.2重量部〜1.0重量部、水30重量部〜
80重量部、好ましくは40重量部〜60重量部であ
る。また、焼却灰に含有されるシリカ又はアルミナ各々
の成分比は50%以上、好ましくは60%以上、焼却灰
にシリカとアルミナ双方が含まれている場合には、シリ
カとアルミナ双方合計の成分比が、50%以上、好まし
くは60%以上であることが望ましい。尚、硬化遅延剤
を添加する場合には、焼却灰100重量部当たり、0.
01重量部〜10重量部、好ましくは0.2重量部〜2
0重量部であることが望ましい。The above-mentioned photocatalyst, caking agent, lime supersaturating agent, and water are blended in amounts of 1 part by weight to 10 parts by weight, preferably 3 parts by weight to 7 parts by weight of the photocatalyst per 100 parts by weight of incinerated ash. 10 to 70 parts by weight, preferably 20 to 6 parts by weight
0 part by weight, lime supersaturating agent 0.01 part by weight to 5 parts by weight, preferably 0.2 part by weight to 1.0 part by weight, water 30 parts by weight to
80 parts by weight, preferably 40 to 60 parts by weight. Further, the component ratio of each of silica and alumina contained in the incinerated ash is 50% or more, preferably 60% or more. Is 50% or more, preferably 60% or more. When a curing retarder is added, it is added to 100 parts by weight of incinerated ash.
01 to 10 parts by weight, preferably 0.2 to 2 parts by weight
It is preferably 0 parts by weight.
【0023】尚、本発明の実施に際しては、上記の光触
媒、固結剤、石灰過飽和剤等の主成分の他に、必要に応
じてセメント混和剤として用いられている減水剤、流動
化剤、起泡剤、凝結促進剤、凝結遅延剤、膨張剤、高分
子エマルジョン、骨材等を添加してもよい。In carrying out the present invention, in addition to the above-mentioned main components such as the photocatalyst, the solidifying agent and the lime supersaturating agent, a water reducing agent, a fluidizing agent, which is optionally used as a cement admixture, A foaming agent, a setting accelerator, a setting retarder, a swelling agent, a polymer emulsion, an aggregate and the like may be added.
【0024】以下に、活性汚泥焼却灰を利用して光触媒
の固結生成物を得る場合の配合例を示す。 The following is an example of blending in the case of obtaining a solidified product of a photocatalyst by using activated sludge incineration ash.
【0025】上記の活性汚泥焼却灰は、上記のシリカ
(SiO2 )及びアルミナ(Al2O3)の他に、Fe2
O3(9.11%)、MnO(0.18%)、TiO
2(1.07%)、CaO(9.32%)、MgO
(2.86%)、K2O(0.27%)、 P2O5(1
5.6%)を含むものである。The above activated sludge incineration ash contains Fe 2 in addition to the above silica (SiO 2 ) and alumina (Al 2 O 3 ).
O 3 (9.11%), MnO (0.18%), TiO
2 (1.07%), CaO (9.32%), MgO
(2.86%), K 2 O (0.27%), P 2 O 5 (1
5.6%).
【0026】上記配合例は、活性汚泥焼却灰からレンガ
様の硬化物を製造する場合の配合であり、型枠に流し込
んで成型可能な程度の流動性を有し、型枠に流し込んだ
後約1時間で硬化するものである。The above formulation example is a formulation for producing a brick-like cured product from activated sludge incineration ash, which has a fluidity such that it can be poured into a mold to be molded, and after being poured into the mold, about It cures in 1 hour.
【0027】上記配合例で得られる光触媒の固結生成物
は、比重が約1.4で、単位重量当たりの吸水量は36
%である。この比重と吸水量は、配合水量により変化
し、また起泡剤の添加により軽量化される。The solidified product of the photocatalyst obtained in the above formulation example has a specific gravity of about 1.4 and a water absorption amount per unit weight of 36.
%. The specific gravity and the amount of water absorption vary depending on the amount of blended water, and the addition of a foaming agent reduces the weight.
【0028】尚、上記の活性汚泥焼却灰の如く、シリ
カ、アルミナ以外にも各種の金属酸化物が含まれている
場合には、固結反応が一層促進される。Incidentally, when various metal oxides other than silica and alumina are contained as in the above activated sludge incineration ash, the solidification reaction is further promoted.
【0029】また、Fe2O3、MnO、CuOは触媒効
果を高めることから、これら成分を含む焼却灰を使用し
て光触媒の固結生成物を製造するのが望ましい。Further, since Fe 2 O 3 , MnO and CuO enhance the catalytic effect, it is desirable to produce the solidified product of the photocatalyst by using the incinerated ash containing these components.
【0030】さらに、焼却灰中にFe2O3、CuO、P
bO等が含有されている場合には、酸化銀の粉末を用い
なくとも、安価な硝酸銀(AgNO3 )を添加すること
で、この硝酸銀が上記Fe2O3やCuOあるいはPbO
と反応して光触媒である酸化銀(AgO、Ag2O )が
形成されるため、低コストで光触媒の固結生成物を得る
ことができる。Furthermore, Fe 2 O 3 , CuO and P are contained in the incinerated ash.
When bO or the like is contained, the silver nitrate can be added to the Fe 2 O 3 or CuO or PbO by adding inexpensive silver nitrate (AgNO 3 ) without using silver oxide powder.
Reacts with silver oxide (AgO, Ag 2 O), which is a photocatalyst, to form a solidified product of the photocatalyst at low cost.
【0031】尚、上記した如く焼却灰を利用して光触媒
の固結生成物を製造する場合においては、焼却灰中に重
金属類、有害物質及び悪臭物質が含まれている場合が多
いことから、これらを封止する吸収剤を添加することが
望ましい。この吸収剤は、例えば、重金属捕捉作用のあ
るゼオライト、大谷石粉などの天然イオン交換作用物
質、重金属及び悪臭物質を吸着する活性炭、またはリン
酸ソーダ、EDTA2Na、粉末イオン交換樹脂などが
挙げられる。尚、上記の吸着剤では不十分なほど、多量
の重金属を含有する焼却灰を利用する場合には、3〜4
号硅酸1モル/アルミナセメント2モル以上又はアルミ
ニウム塩1モル以上の合成ゼオライトで、焼却灰を包み
込んで処理した後、固結剤・水和剤を添加して固結生成
物を製造してもよい。When the solidified product of the photocatalyst is produced by using the incinerated ash as described above, since the incinerated ash often contains heavy metals, harmful substances and malodorous substances, It is desirable to add an absorbent that seals them. Examples of the absorbent include heavy metal-trapping zeolite, natural ion-exchange substances such as Otaniishi powder, activated carbon that adsorbs heavy metals and malodorous substances, sodium phosphate, EDTA2Na, and powder ion-exchange resins. In addition, when the incineration ash containing a large amount of heavy metals is used to the extent that the above-mentioned adsorbent is insufficient, it is 3 to 4
No. 1 mol of silicic acid / 2 mol or more of alumina cement or 1 mol or more of aluminum salt is used to wrap the incineration ash and treat it, and then to add a solidifying agent and a wettable powder to produce a solidified product. Good.
【0032】上記の通り、本実施例では、光触媒にシリ
カ、アルミナを含有する焼却灰と、生石灰及びセメント
混合物を含有する固結剤と、石灰過飽和材を含有する水
和調節剤を主成分とする添加剤と、水とを加えて混合
し、ポゾラン反応を利用して常温で光触媒を固結したこ
とから、従来の高温で焼結固化する場合に比べて、低コ
ストで光触媒の固結生成物を得ることができる。また、
光触媒が酸化チタンの場合には、触媒活性の高いアナタ
ーゼ型の固結生成物を得ることができる。さらに、廃棄
物である焼却灰を、光触媒の固結生成物として有効に再
資源化することができる。As described above, in the present embodiment, the main components are the incineration ash containing silica and alumina as the photocatalyst, the solidifying agent containing the quick lime and the cement mixture, and the hydration regulator containing the lime supersaturated material. Additives and water are added and mixed, and the photocatalyst is solidified at room temperature by using the pozzolan reaction, so the solidification of the photocatalyst can be produced at a lower cost than the conventional case of sintering and solidification at high temperature. You can get things. Also,
When the photocatalyst is titanium oxide, an anatase-type solidified product having high catalytic activity can be obtained. Furthermore, the incineration ash that is a waste can be effectively recycled as a solidified product of the photocatalyst.
【0033】また、常温で光触媒を固結することから、
図1に示すように、光触媒の固結生成物1の内部に光源
2を入れた状態で固結することができ、固結生成物1の
光触媒作用を高めることが可能となる。この場合には、
光源2からの光が透過するように、固結生成物1を発泡
させたり、或いは固結生成物1に穴を形成することので
きる形状の型枠を用意して固結させる。Since the photocatalyst is solidified at room temperature,
As shown in FIG. 1, it is possible to solidify the photocatalyst solidified product 1 with the light source 2 inside, and to enhance the photocatalytic action of the solidified product 1. In this case,
The solidified product 1 is foamed so that the light from the light source 2 is transmitted, or a mold having a shape capable of forming a hole in the solidified product 1 is prepared and solidified.
【0034】尚、焼却灰を利用した光触媒の固結生成物
は、例えば擬石、擬木、ブロック、彫刻等として製作
し、これを室内や公園等の屋外に設置することにより、
窒素酸化物(NOx )、硫黄酸化物(SOx )、オゾン
(O3 )等の有害物質の分解、悪臭物質の分解、殺菌等
に利用することができる。また、焼却灰を利用した光触
媒の固結生成物を護岸ブロックとして製作し、これを河
川底や沼底に配置することにより、水中のトリクロンや
トリエタン等の有害有機物や汚濁物の分解に利用するこ
とができる。The solidified product of the photocatalyst using the incinerated ash is produced as, for example, pseudo stone, artificial wood, block, sculpture, etc., and is installed indoors or outdoors such as in a park,
It can be used for decomposing harmful substances such as nitrogen oxides (NO x ), sulfur oxides (SO x ), ozone (O 3 ), decomposing odorous substances, and sterilizing. In addition, a solidified product of photocatalyst that uses incinerated ash is manufactured as a revetment block and placed on the bottom of rivers or swamps to be used for the decomposition of harmful organic substances and pollutants such as trichlorne and triethane in water. be able to.
【0035】[0035]
【発明の効果】本発明の光触媒の固結方法によれば、光
触媒に、シリカ、アルミナの少なくとも1種と、生石灰
及びセメント混合物を含有する固結剤と、石灰過飽和材
を含有する水和調節剤を主成分とする添加剤と、水とを
加えて混合し、硬化させるものであることから、光触媒
を焼結することなく、ポゾラン反応を利用して常温で固
化することができる。According to the method for consolidating a photocatalyst of the present invention, the photocatalyst contains at least one of silica and alumina, a consolidating agent containing a mixture of quick lime and cement, and a hydration adjusting agent containing a lime supersaturated material. Since the additive containing the agent as a main component and water are added and mixed and cured, the photocatalyst can be solidified at room temperature by utilizing the pozzolan reaction without sintering.
【0036】また、光触媒に、シリカ、アルミナの少な
くとも1種を含有する焼却灰と、生石灰及びセメント混
合物を含有する固結剤と、石灰過飽和材を含有する水和
調節剤を主成分とする添加剤と、水とを加えて混合し、
硬化させるものであることから、廃棄物の焼却灰を光触
媒の固結生成物として有効に再資源化できる。In addition, an incineration ash containing at least one of silica and alumina, a solidifying agent containing quick lime and a cement mixture, and a hydration modifier containing a lime supersaturant as main components are added to the photocatalyst. Add the agent and water and mix,
Since it cures, incineration ash of waste can be effectively recycled as a solidified product of the photocatalyst.
【図1】内部に光源を入れた光触媒の固結生成物を示す
断面図である。FIG. 1 is a cross-sectional view showing a solidified product of a photocatalyst having a light source inside.
1 光触媒の固結生成物 2 光源 1 Solidified product of photocatalyst 2 Light source
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01J 37/00 B01J 37/00 J ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Office reference number FI technical display location B01J 37/00 B01J 37/00 J
Claims (3)
1種と、生石灰及びセメント混合物を含有する固結剤
と、石灰過飽和材を含有する水和調節剤を主成分とする
添加剤と、水とを加えて混合し、硬化させることを特徴
とする光触媒の固結方法。1. A photocatalyst containing at least one of silica and alumina, a solidifying agent containing quicklime and a cement mixture, an additive containing a hydration regulator containing a lime supersaturating agent as a main component, and water. A method of consolidating a photocatalyst, which comprises adding, mixing and curing.
1種を含有する焼却灰と、生石灰及びセメント混合物を
含有する固結剤と、石灰過飽和材を含有する水和調節剤
を主成分とする添加剤と、水とを加えて混合し、硬化さ
せることを特徴とする光触媒の固結方法。2. A photocatalyst containing incineration ash containing at least one of silica and alumina, a solidifying agent containing quicklime and a cement mixture, and a hydration modifier containing a lime supersaturant as main components. A method for consolidating a photocatalyst, which comprises adding an agent and water, mixing and curing.
鉛、酸化タングステンのいずれかであることを特徴とす
る請求項1又は2記載の光触媒の固結方法。3. The method for consolidating a photocatalyst according to claim 1, wherein the photocatalyst is any one of titanium oxide, silver oxide, zinc oxide and tungsten oxide.
Priority Applications (1)
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JP25815595A JP2913265B2 (en) | 1995-09-11 | 1995-09-11 | Photocatalyst consolidation method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
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JP25815595A JP2913265B2 (en) | 1995-09-11 | 1995-09-11 | Photocatalyst consolidation method |
Publications (2)
Publication Number | Publication Date |
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JPH0975747A true JPH0975747A (en) | 1997-03-25 |
JP2913265B2 JP2913265B2 (en) | 1999-06-28 |
Family
ID=17316297
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Cited By (10)
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JPH09230105A (en) * | 1995-12-22 | 1997-09-05 | Toto Ltd | Antifogging method and facility applied with the method |
EP0885857A1 (en) * | 1997-06-19 | 1998-12-23 | Italcementi S.p.A. | Use of organic additives for the preparation of cementitious compositions with improved properties of constancy of colour |
JP2000117117A (en) * | 1998-10-12 | 2000-04-25 | Mitsubishi Materials Corp | Photocatalytic material |
JP2001253754A (en) * | 2001-02-26 | 2001-09-18 | Mitsubishi Materials Corp | Cement article for purifying atmosphere |
JP2002087861A (en) * | 2000-09-18 | 2002-03-27 | Denki Kagaku Kogyo Kk | Cement admixing agent and cement composition |
JP2003089566A (en) * | 2002-07-15 | 2003-03-28 | Mitsubishi Materials Corp | Cement product for cleaning atmosphere |
JP2007275767A (en) * | 2006-04-06 | 2007-10-25 | Earth Kensetsu Consultant Kk | Photocatalyst-deposited granular substance, and package for air clarification and grass-proofing using the same |
US7300514B2 (en) * | 2002-10-03 | 2007-11-27 | Ciments Francais | Photocatalytic granular mixture for mortar and concrete and its use |
JP2008142606A (en) * | 2006-12-07 | 2008-06-26 | New Industry Research Organization | Photocatalyst composition, photocatalyst material and its manufacturing method |
JP2010253437A (en) * | 2009-04-28 | 2010-11-11 | Nittetsu Kankyo Engineering Kk | Method for treating organic wastewater and chemical used for the method for treating the same |
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JP2007275767A (en) * | 2006-04-06 | 2007-10-25 | Earth Kensetsu Consultant Kk | Photocatalyst-deposited granular substance, and package for air clarification and grass-proofing using the same |
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