CN109365005B - Photocatalyst hydrosol with high catalytic degradation performance and production process thereof - Google Patents
Photocatalyst hydrosol with high catalytic degradation performance and production process thereof Download PDFInfo
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- 230000015556 catabolic process Effects 0.000 title claims abstract description 77
- 238000006731 degradation reaction Methods 0.000 title claims abstract description 77
- 239000011941 photocatalyst Substances 0.000 title claims abstract description 74
- 230000003197 catalytic effect Effects 0.000 title claims abstract description 70
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 23
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims abstract description 149
- 238000003756 stirring Methods 0.000 claims abstract description 88
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 77
- 239000004408 titanium dioxide Substances 0.000 claims abstract description 73
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 51
- DKUYEPUUXLQPPX-UHFFFAOYSA-N dibismuth;molybdenum;oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[O-2].[Mo].[Mo].[Bi+3].[Bi+3] DKUYEPUUXLQPPX-UHFFFAOYSA-N 0.000 claims abstract description 50
- 229910021389 graphene Inorganic materials 0.000 claims abstract description 49
- 239000000839 emulsion Substances 0.000 claims abstract description 46
- 239000011259 mixed solution Substances 0.000 claims abstract description 46
- 229910001868 water Inorganic materials 0.000 claims abstract description 46
- BUGBHKTXTAQXES-UHFFFAOYSA-N Selenium Chemical compound [Se] BUGBHKTXTAQXES-UHFFFAOYSA-N 0.000 claims abstract description 44
- 229910052711 selenium Inorganic materials 0.000 claims abstract description 33
- 239000011669 selenium Substances 0.000 claims abstract description 33
- 239000002131 composite material Substances 0.000 claims abstract description 29
- 238000002360 preparation method Methods 0.000 claims abstract description 26
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims abstract description 20
- GCLGEJMYGQKIIW-UHFFFAOYSA-H sodium hexametaphosphate Chemical compound [Na]OP1(=O)OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O1 GCLGEJMYGQKIIW-UHFFFAOYSA-H 0.000 claims abstract description 15
- 235000019982 sodium hexametaphosphate Nutrition 0.000 claims abstract description 15
- 239000001577 tetrasodium phosphonato phosphate Substances 0.000 claims abstract description 15
- 230000001804 emulsifying effect Effects 0.000 claims abstract description 14
- 238000010008 shearing Methods 0.000 claims abstract description 14
- 239000003381 stabilizer Substances 0.000 claims abstract description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 108
- 238000006243 chemical reaction Methods 0.000 claims description 88
- 239000000243 solution Substances 0.000 claims description 69
- 239000007787 solid Substances 0.000 claims description 50
- 239000007795 chemical reaction product Substances 0.000 claims description 40
- 239000007864 aqueous solution Substances 0.000 claims description 37
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 36
- 239000008367 deionised water Substances 0.000 claims description 32
- 229910021641 deionized water Inorganic materials 0.000 claims description 32
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 30
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 claims description 28
- 239000007788 liquid Substances 0.000 claims description 28
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 27
- 229910017604 nitric acid Inorganic materials 0.000 claims description 27
- YRKCREAYFQTBPV-UHFFFAOYSA-N acetylacetone Chemical compound CC(=O)CC(C)=O YRKCREAYFQTBPV-UHFFFAOYSA-N 0.000 claims description 25
- 238000001132 ultrasonic dispersion Methods 0.000 claims description 25
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 claims description 22
- 239000006185 dispersion Substances 0.000 claims description 22
- 238000001035 drying Methods 0.000 claims description 22
- 239000002244 precipitate Substances 0.000 claims description 22
- 238000005406 washing Methods 0.000 claims description 22
- 238000001816 cooling Methods 0.000 claims description 18
- 238000007789 sealing Methods 0.000 claims description 17
- FBXVOTBTGXARNA-UHFFFAOYSA-N bismuth;trinitrate;pentahydrate Chemical compound O.O.O.O.O.[Bi+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O FBXVOTBTGXARNA-UHFFFAOYSA-N 0.000 claims description 13
- HHDOORYZQSEMGM-UHFFFAOYSA-L potassium;oxalate;titanium(4+) Chemical compound [K+].[Ti+4].[O-]C(=O)C([O-])=O HHDOORYZQSEMGM-UHFFFAOYSA-L 0.000 claims description 12
- RWVGQQGBQSJDQV-UHFFFAOYSA-M sodium;3-[[4-[(e)-[4-(4-ethoxyanilino)phenyl]-[4-[ethyl-[(3-sulfonatophenyl)methyl]azaniumylidene]-2-methylcyclohexa-2,5-dien-1-ylidene]methyl]-n-ethyl-3-methylanilino]methyl]benzenesulfonate Chemical compound [Na+].C1=CC(OCC)=CC=C1NC1=CC=C(C(=C2C(=CC(C=C2)=[N+](CC)CC=2C=C(C=CC=2)S([O-])(=O)=O)C)C=2C(=CC(=CC=2)N(CC)CC=2C=C(C=CC=2)S([O-])(=O)=O)C)C=C1 RWVGQQGBQSJDQV-UHFFFAOYSA-M 0.000 claims description 12
- 238000002156 mixing Methods 0.000 claims description 11
- 239000013049 sediment Substances 0.000 claims description 9
- 238000002791 soaking Methods 0.000 claims description 9
- 235000011187 glycerol Nutrition 0.000 claims description 8
- 239000004005 microsphere Substances 0.000 claims description 8
- 238000000034 method Methods 0.000 claims description 7
- 235000019441 ethanol Nutrition 0.000 claims description 5
- 239000000203 mixture Substances 0.000 claims description 5
- LCTONWCANYUPML-UHFFFAOYSA-N Pyruvic acid Chemical compound CC(=O)C(O)=O LCTONWCANYUPML-UHFFFAOYSA-N 0.000 claims description 4
- HHLFWLYXYJOTON-UHFFFAOYSA-N glyoxylic acid Chemical compound OC(=O)C=O HHLFWLYXYJOTON-UHFFFAOYSA-N 0.000 claims description 4
- 239000012295 chemical reaction liquid Substances 0.000 claims description 2
- 229940107700 pyruvic acid Drugs 0.000 claims description 2
- 239000012046 mixed solvent Substances 0.000 claims 1
- 230000001699 photocatalysis Effects 0.000 abstract description 10
- 230000031700 light absorption Effects 0.000 abstract description 6
- 239000002245 particle Substances 0.000 abstract description 6
- SPSSULHKWOKEEL-UHFFFAOYSA-N 2,4,6-trinitrotoluene Chemical compound CC1=C([N+]([O-])=O)C=C([N+]([O-])=O)C=C1[N+]([O-])=O SPSSULHKWOKEEL-UHFFFAOYSA-N 0.000 description 54
- 239000000015 trinitrotoluene Substances 0.000 description 54
- 230000003595 spectral effect Effects 0.000 description 24
- STZCRXQWRGQSJD-GEEYTBSJSA-M methyl orange Chemical compound [Na+].C1=CC(N(C)C)=CC=C1\N=N\C1=CC=C(S([O-])(=O)=O)C=C1 STZCRXQWRGQSJD-GEEYTBSJSA-M 0.000 description 18
- 229940012189 methyl orange Drugs 0.000 description 18
- 238000002835 absorbance Methods 0.000 description 16
- 238000010521 absorption reaction Methods 0.000 description 16
- 238000005259 measurement Methods 0.000 description 8
- 239000000843 powder Substances 0.000 description 8
- 239000010453 quartz Substances 0.000 description 8
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 8
- 238000001228 spectrum Methods 0.000 description 8
- 238000009210 therapy by ultrasound Methods 0.000 description 8
- 238000012546 transfer Methods 0.000 description 8
- 238000000870 ultraviolet spectroscopy Methods 0.000 description 8
- 230000005284 excitation Effects 0.000 description 7
- 239000000463 material Substances 0.000 description 6
- 239000003574 free electron Substances 0.000 description 5
- 230000009471 action Effects 0.000 description 4
- MTHSVFCYNBDYFN-UHFFFAOYSA-N diethylene glycol Chemical compound OCCOCCO MTHSVFCYNBDYFN-UHFFFAOYSA-N 0.000 description 3
- 238000013033 photocatalytic degradation reaction Methods 0.000 description 3
- 238000013032 photocatalytic reaction Methods 0.000 description 3
- 238000005215 recombination Methods 0.000 description 3
- 230000006798 recombination Effects 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- YLSLSHTYFFBCKG-UHFFFAOYSA-N bismuth;oxomolybdenum Chemical compound [Mo].[Bi]=O YLSLSHTYFFBCKG-UHFFFAOYSA-N 0.000 description 2
- KBPLFHHGFOOTCA-UHFFFAOYSA-N caprylic alcohol Natural products CCCCCCCCO KBPLFHHGFOOTCA-UHFFFAOYSA-N 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 230000007547 defect Effects 0.000 description 2
- 239000011159 matrix material Substances 0.000 description 2
- 230000005012 migration Effects 0.000 description 2
- 238000013508 migration Methods 0.000 description 2
- 239000002086 nanomaterial Substances 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 125000004430 oxygen atom Chemical group O* 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 230000027756 respiratory electron transport chain Effects 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 241000233866 Fungi Species 0.000 description 1
- 125000004429 atom Chemical group 0.000 description 1
- 238000004332 deodorization Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- UHWHMHPXHWHWPX-UHFFFAOYSA-J dipotassium;oxalate;oxotitanium(2+) Chemical compound [K+].[K+].[Ti+2]=O.[O-]C(=O)C([O-])=O.[O-]C(=O)C([O-])=O UHWHMHPXHWHWPX-UHFFFAOYSA-J 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- TVMXDCGIABBOFY-UHFFFAOYSA-N n-Octanol Natural products CCCCCCCC TVMXDCGIABBOFY-UHFFFAOYSA-N 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 125000001997 phenyl group Chemical group [H]C1=C([H])C([H])=C(*)C([H])=C1[H] 0.000 description 1
- 238000007146 photocatalysis Methods 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000011877 solvent mixture Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000003053 toxin Substances 0.000 description 1
- 231100000765 toxin Toxicity 0.000 description 1
- 108700012359 toxins Proteins 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J31/00—Catalysts comprising hydrides, coordination complexes or organic compounds
- B01J31/26—Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
- B01J31/38—Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of titanium, zirconium or hafnium
-
- B01J35/23—
-
- B01J35/39—
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/34—Organic compounds containing oxygen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/38—Organic compounds containing nitrogen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/40—Organic compounds containing sulfur
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/10—Photocatalysts
Abstract
The invention discloses a photocatalyst hydrosol with high catalytic degradation performance and a production process thereof. The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding sodium hexametaphosphate into water, and stirring to obtain a mixed solution; adding titanium dioxide or a titanium dioxide/graphene composite material and bismuth molybdate or selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring; then adding hydrogen peroxide solution, shearing, emulsifying and standing to obtain emulsion; and adding a stabilizer into the emulsion, continuously stirring, and then adjusting the pH value to obtain the photocatalyst hydrosol with high catalytic degradation performance. The photocatalyst hydrosol with high catalytic degradation performance, which is obtained by the invention, has the advantages of uniform particle size, good dispersibility, high stability, excellent light absorption performance, good photocatalytic effect, stable performance, simple preparation process, mild preparation conditions and good application value.
Description
Technical Field
The invention relates to the technical field of photocatalysts, in particular to a photocatalyst hydrosol with high catalytic degradation performance and a production process thereof.
Background
The photocatalyst is a nano-scale metal oxide material, is coated on the surface of a base material, generates a strong catalytic function under the action of light, and can effectively degrade toxic and harmful gases in the air; killing various bacteria, and decomposing or harmlessly treating toxins released by the bacteria or fungi; meanwhile, the photocatalyst also has the functions of deodorization, stain resistance and the like. The essential condition for the photocatalytic action is the presence of a photocatalyst and illumination of a suitable wavelength. The most common photocatalyst is titanium dioxide material at present. The photocatalytic effect of titanium dioxide is determined by its own physicochemical properties. The forbidden band width of titanium dioxide is 3.2eV, and the corresponding light absorption wavelength is 387nm, which means that only when the titanium dioxide is irradiated by light with the wavelength less than or equal to the wavelength, the titanium dioxide can play a role of photocatalysis, electrons on the valence band can be excited to cross the forbidden band and enter the conduction band, corresponding holes are generated on the valence band, and the conduction band electrons and the valence band holes generated by light excitation have enough service life before recombination.
The contradiction between the development of the 21 st century and the environment is increasingly prominent, the attention and research of researchers in the field of photocatalytic environmental protection are gradually increased, and especially the photocatalytic degradation of organic pollutants in wastewater is one of the hottest research subjects. Titanium dioxide has very high photocatalytic properties as an economical environmentally friendly material, and has been receiving much attention from researchers in the recent years. However, the titanium dioxide has a large forbidden band width (rutile phase is 3.0eV, and anatase phase is 3.2eV), and can only be excited by ultraviolet light, which severely limits the catalytic activity and practical use conditions; on the other hand, when the titanium dioxide is irradiated by light, excited electron-hole pairs cannot be timely transferred to the surface, are rapidly recombined in the titanium dioxide, cannot play a catalytic effect, and also reduce the catalytic activity of the titanium dioxide.
Disclosure of Invention
The invention aims to provide a production process of the photocatalyst hydrosol with high catalytic degradation performance, and the photocatalyst hydrosol with high catalytic degradation performance obtained by the process has the advantages of uniform particle size, good dispersibility, high stability, excellent light absorption performance, good photocatalytic effect, stable performance, simple preparation process and mild preparation conditions.
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding sodium hexametaphosphate into water, and stirring to obtain a mixed solution; adding titanium dioxide or a titanium dioxide/graphene composite material and bismuth molybdate or selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring; then adding hydrogen peroxide solution, shearing, emulsifying and standing to obtain emulsion; and adding a stabilizer into the emulsion, continuously stirring, and then adjusting the pH value to obtain the photocatalyst hydrosol with high catalytic degradation performance.
As one of the preferable technical schemes of the invention, the production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 0.2-1 g of sodium hexametaphosphate into 200-300 g of water, and stirring for 10-20 minutes to obtain a mixed solution; adding 2-6 g of titanium dioxide or titanium dioxide/graphene composite material into the mixed solution, and continuously stirring for 5-15 minutes; then adding 2-6 g of hydrogen peroxide solution with the mass fraction of 10-20%, shearing and emulsifying for 20-40 minutes, and standing for 12-14 hours to obtain an emulsion; and adding 0.2-1 g of stabilizer into the emulsion, continuously stirring for 10-20 minutes, and then adjusting the pH value to 7-8 to obtain the photocatalyst hydrosol with high catalytic degradation performance.
As the second preferred technical scheme of the invention, the production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 0.2-1 g of sodium hexametaphosphate into 200-300 g of water, and stirring for 10-20 minutes to obtain a mixed solution; adding 2-6 g of titanium dioxide or titanium dioxide/graphene composite material and 1-3 g of bismuth molybdate or selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring for 5-15 minutes; then adding 2-6 g of hydrogen peroxide solution with the mass fraction of 10-20%, shearing and emulsifying for 20-40 minutes, and standing for 12-14 hours to obtain an emulsion; and adding 0.2-1 g of stabilizer into the emulsion, continuously stirring for 10-20 minutes, and then adjusting the pH value to 7-8 to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the bismuth molybdate comprises the following steps: adding 4-5 g of bismuth nitrate pentahydrate and 0.5-1 g of sodium molybdate dihydrate into 300-600 mL of water, stirring for 20-40 minutes, and performing ultrasonic dispersion for 10-15 minutes to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 100-300 mL of absolute ethyl alcohol, uniformly mixing, sealing the reaction system, and reacting at 150-180 ℃ for 6-12 hours; centrifuging the reaction solution, and collecting precipitate; and washing the precipitate with water and absolute ethyl alcohol in sequence, and drying to obtain the bismuth molybdate.
The preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4-5 g of bismuth nitrate pentahydrate, 0.5-1 g of sodium molybdate dihydrate and 0.2-0.5 g of selenium powder into 300-600 mL of water, stirring for 20-40 minutes, and performing ultrasonic dispersion for 10-15 minutes to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 100-300 mL of absolute ethyl alcohol, uniformly mixing, sealing the reaction system, and reacting at 150-180 ℃ for 6-12 hours; centrifuging the reaction solution, and collecting precipitate; and washing the precipitate with water and absolute ethyl alcohol in sequence, and drying to obtain the selenium-loaded bismuth molybdate.
The preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16-20 g of sodium hydroxide into 30-50 mL of water, stirring for 30-60 minutes, and naturally cooling to 20-30 ℃ to prepare a sodium hydroxide aqueous solution; adding 1-2 g of titanium dioxide into an aqueous solution of sodium hydroxide, and continuously stirring for 30-60 minutes to obtain an emulsion; adding 0.1-0.3 g of graphene into the emulsion, stirring for 10-30 minutes, and performing ultrasonic dispersion for 10-25 minutes to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 6-12 hours at 180-200 ℃; after the reaction is finished, naturally cooling the reaction system to 20-30 ℃, centrifuging, and collecting bottom sediment to obtain a reaction product; placing the reaction product in nitric acid with the molar concentration of 0.1-0.5 mol/L for soaking for 10-12 hours, centrifuging, and collecting bottom solids; and washing the bottom solid with water and absolute ethyl alcohol in sequence, and drying to obtain the titanium dioxide/graphene composite material.
Further, the preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16-20 g of sodium hydroxide into 10-30 mL of water and 10-30 mL of organic alcohol, stirring for 30-60 minutes, and naturally cooling to 20-30 ℃ to prepare a sodium hydroxide aqueous solution; adding 1-2 g of titanium dioxide into an aqueous solution of sodium hydroxide, and continuously stirring for 30-60 minutes to obtain an emulsion; adding 0.1-0.3 g of graphene into the emulsion, stirring for 10-30 minutes, and performing ultrasonic dispersion for 10-25 minutes to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 6-12 hours at 180-200 ℃; after the reaction is finished, naturally cooling the reaction system to 20-30 ℃, centrifuging, and collecting bottom sediment to obtain a reaction product; placing the reaction product in nitric acid with the molar concentration of 0.1-0.5 mol/L for soaking for 10-12 hours, centrifuging, and collecting bottom solids; washing the bottom solid with water and absolute ethyl alcohol in sequence, and drying to obtain a titanium dioxide/graphene composite material; the organic alcohol is one or a mixture of more of ethylene glycol, diethylene glycol, n-octanol and glycerol. Preferably, the organic alcohol is ethylene glycol and glycerol in a volume ratio of (1-3): (1-3) in the presence of a solvent mixture.
Further, the titanium dioxide is in a hollow microsphere structure and is obtained by the following method: dissolving titanium potassium oxalate and nitric acid in a hydrogen peroxide solution with the mass fraction of 10-20% to ensure that the concentration of the titanium potassium oxalate is 300-600 mmol/L and the concentration of the nitric acid is 0.6-0.9 mmol/L to obtain a reaction solution; placing the prepared reaction liquid into a reaction kettle, sealing the reaction system, and reacting at the constant temperature of 40-50 ℃ for 48-72 hours; after the reaction is finished, centrifuging and collecting bottom solids; and (3) sequentially washing the bottom solid with 0.1mol/L hydrochloric acid and water respectively, drying at 60-80 ℃, and treating for 1-2 hours at 400-500 ℃ in an air atmosphere.
The stabilizer is one or a mixture of more of acetylacetone, pyruvic acid and glyoxylic acid.
Compared with the prior art, the invention has the following advantages:
1. bismuth molybdate is a typical bismuth-molybdenum oxide, and is formed by bonding two functional oxides. The bismuth molybdate has a unique structure and a proper forbidden band width, and shows better catalytic activity under the irradiation of sunlight. The invention is different from the prior art that titanium dioxide is generally adopted as a carrier of the photocatalyst, and the titanium dioxide and bismuth molybdate are combined for use, so that the application range of the photocatalyst is widened, and the catalytic efficiency is enhanced.
2. Selenium and oxygen atoms have stronger bonding force, so that the surface of bismuth molybdate is greatly improved in the aspects of light absorption, electron transfer, electron hole separation and the like. The selenium-loaded bismuth molybdate replaces bismuth molybdate, so that the capability of the photocatalyst hydrosol for forming free electrons and holes under the excitation action of visible light is enhanced.
3. The graphene serving as the carbon nano material with the monoatomic layer structure has excellent electrical characteristics and is a good electron acceptor. The graphene is introduced into the field of photocatalytic degradation, and through the controllable combination with titanium dioxide, the defect of the titanium dioxide can be effectively made up, the photocatalytic property is greatly improved, the migration path of a photo-excited carrier to the surface of a material is effectively shortened, and the efficiency reduction caused by internal recombination is reduced; the ultrahigh carrier mobility of the graphene is utilized to rapidly separate electrons and holes generated by excitation, and participate in organic molecule decomposition reaction, so that the catalytic efficiency is improved.
4. The titanium dioxide with the hollow microsphere structure is combined with the porous structure and the ultrahigh specific surface area of the graphene, so that the contact area between the photocatalyst hydrosol and the degradation matrix is increased, organic molecules can be effectively adsorbed, and the photocatalytic reaction is facilitated. In addition, the graphene has certain mechanical strength, can be used as a support body, and is convenient to recycle integrally.
The second purpose of the invention is to provide a photocatalyst hydrosol with high catalytic degradation performance, which is prepared by adopting any one of the production processes of the photocatalyst hydrosol with high catalytic degradation performance.
The photocatalyst hydrosol with high catalytic degradation performance, which is obtained by the invention, has the advantages of uniform particle size, good dispersibility, high stability, excellent light absorption performance, good photocatalytic effect, stable performance, simple preparation process, mild preparation conditions and good application value.
Detailed Description
The raw materials in the examples are as follows:
sodium hexametaphosphate, CAS number: 10124-56-8.
Titanium dioxide, CAS No.: 13463-67-7, available from Bailingwei science and technology Co., Ltd., particle size 50 nm.
Bismuth nitrate pentahydrate, CAS No.: 10035-06-0.
Sodium molybdate dihydrate, CAS No.: 10102-42-6.
Selenium powder, CAS No.: 7782-49-2, supplied by Wuhan Rifame resources trade Co., Ltd., particle size 200 mesh, origin Japan.
Graphene, offered by yohimoto chemical products limited in Henan, cat No. 040, CAS no: 608-32-18, diameter of 1-12 μm, thickness of 5-15 nm, density of 2.25g/cm3。
Ethylene glycol, CAS No.: 107-21-1.
Potassium titanium oxalate, CAS No.: 14481-26-6.
Acetylacetone, CAS No.: 123-54-6.
Glycerol, CAS number: 56-81-5.
Example 1
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 5g of titanium dioxide into the mixed solution, and continuing stirring at 80 rpm for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 1 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The measured spectrum scanning curve absorption area is 369.7nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then pouring 10mg/L of TNT solution into a quartz culture dish, adding 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 1, standing for 24 hours in a completely dark environment, and performing ultrasonic dispersion uniformly. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. Through measurement, the degradation rate of the TNT solution reaches 63.2%. TNT was replaced by methyl orange and it was found that after 5 hours the degradation rate of the aqueous solution of methyl orange reached 68.6%.
Example 2
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide and 1g of bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate and 0.97g of sodium molybdate dihydrate into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; and washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the bismuth molybdate.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 2 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The measured spectrum scanning curve absorption area is 514.6nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then pouring 10mg/L of TNT solution into a quartz culture dish, adding 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 2, standing for 24 hours in a completely dark environment, and uniformly dispersing by ultrasonic waves. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. The degradation rate of the TNT solution reaches 71.9 percent through measurement. TNT was replaced by methyl orange and it was found that after 5 hours, the degradation rate of the aqueous solution of methyl orange reached 76.7%.
Example 3
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide and 1g of selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate, 0.97g of sodium molybdate dihydrate and 0.25g of selenium powder into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; and washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the selenium-loaded bismuth molybdate.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 3 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The measured spectrum scanning curve has an absorption area of 587.5nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then pouring 10mg/L of TNT solution into a quartz culture dish, adding 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 3, standing for 24 hours in a completely dark environment, and performing ultrasonic dispersion uniformly. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. Through measurement, the degradation rate of the TNT solution reaches 77.5 percent. TNT was replaced by methyl orange and it was found that after 5 hours, the degradation rate of the aqueous solution of methyl orange reached 83.2%.
Example 4
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide/graphene composite material and 1g of selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate, 0.97g of sodium molybdate dihydrate and 0.25g of selenium powder into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; and washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the selenium-loaded bismuth molybdate.
The preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16g of sodium hydroxide into 40mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and then naturally cooling to 25 ℃ to prepare a sodium hydroxide aqueous solution; adding 1.4g of titanium dioxide into the aqueous solution of sodium hydroxide, and continuously stirring for 60 minutes at 100 revolutions per minute to obtain emulsion; adding 0.2g of graphene into the emulsion, stirring for 10 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 25 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 12 hours at 200 ℃; after the reaction is finished, naturally cooling the reaction system to 25 ℃, centrifuging for 20 minutes at 3000 r/min, and collecting bottom sediment to obtain a reaction product; and (3) soaking the reaction product in nitric acid with the molar concentration of 0.1mol/L for 12 hours, wherein the solid-to-liquid ratio of the reaction product to the nitric acid is 1: 40(g/L), centrifuging for 10-20 minutes at 3000 r/min, and collecting bottom solids; and washing the bottom solid with deionized water which is 230 times of the weight of the bottom solid and absolute ethyl alcohol which is 70 times of the weight of the bottom solid in sequence, and drying at 80 ℃ for 5 hours to obtain the titanium dioxide/graphene composite material.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 4 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The measured spectrum scanning curve has an absorption area of 657.8nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then pouring 10mg/L of TNT solution into a quartz culture dish, adding 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 4, standing for 24 hours in a completely dark environment, and performing ultrasonic dispersion uniformly. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. Through measurement, the degradation rate of the TNT solution reaches 82.4 percent. TNT was replaced by methyl orange, and it was found that after 5 hours, the degradation rate of the aqueous solution of methyl orange reached 89.5%.
Example 5
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide/graphene composite material and 1g of selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate, 0.97g of sodium molybdate dihydrate and 0.25g of selenium powder into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; and washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the selenium-loaded bismuth molybdate.
The preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16g of sodium hydroxide into 20mL of deionized water and 20mL of ethylene glycol, stirring for 30 minutes at 100 revolutions per minute, and then naturally cooling to 25 ℃ to prepare a sodium hydroxide aqueous solution; adding 1.4g of titanium dioxide into the aqueous solution of sodium hydroxide, and continuously stirring for 60 minutes at 100 revolutions per minute to obtain emulsion; adding 0.2g of graphene into the emulsion, stirring for 10 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 25 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 12 hours at 200 ℃; after the reaction is finished, naturally cooling the reaction system to 25 ℃, centrifuging for 20 minutes at 3000 r/min, and collecting bottom sediment to obtain a reaction product; and (3) soaking the reaction product in nitric acid with the molar concentration of 0.1mol/L for 12 hours, wherein the solid-to-liquid ratio of the reaction product to the nitric acid is 1: 40(g/L), centrifuging for 10-20 minutes at 3000 r/min, and collecting bottom solids; and washing the bottom solid with deionized water which is 230 times of the weight of the bottom solid and absolute ethyl alcohol which is 70 times of the weight of the bottom solid in sequence, and drying at 80 ℃ for 5 hours to obtain the titanium dioxide/graphene composite material.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 5 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The measured spectrum scanning curve has an absorption area of 749.3nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then pouring 10mg/L of TNT solution into a quartz culture dish, adding 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 5, standing for 24 hours in a completely dark environment, and performing uniform ultrasonic dispersion. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. Through measurement, the degradation rate of the TNT solution reaches 85.7 percent. TNT was replaced by methyl orange and it was found that after 5 hours, the degradation rate of the aqueous solution of methyl orange reached 91.9%.
Example 6
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide/graphene composite material and 1g of selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate, 0.97g of sodium molybdate dihydrate and 0.25g of selenium powder into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; and washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the selenium-loaded bismuth molybdate.
The preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16g of sodium hydroxide into 20mL of deionized water and 20mL of ethylene glycol, stirring for 30 minutes at 100 revolutions per minute, and then naturally cooling to 25 ℃ to prepare a sodium hydroxide aqueous solution; adding 1.4g of titanium dioxide into the aqueous solution of sodium hydroxide, and continuously stirring for 60 minutes at 100 revolutions per minute to obtain emulsion; adding 0.2g of graphene into the emulsion, stirring for 10 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 25 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 12 hours at 200 ℃; after the reaction is finished, naturally cooling the reaction system to 25 ℃, centrifuging for 20 minutes at 3000 r/min, and collecting bottom sediment to obtain a reaction product; and (3) soaking the reaction product in nitric acid with the molar concentration of 0.1mol/L for 12 hours, wherein the solid-to-liquid ratio of the reaction product to the nitric acid is 1: 40(g/L), centrifuging for 10-20 minutes at 3000 r/min, and collecting bottom solids; and washing the bottom solid with deionized water which is 230 times of the weight of the bottom solid and absolute ethyl alcohol which is 70 times of the weight of the bottom solid in sequence, and drying at 80 ℃ for 5 hours to obtain the titanium dioxide/graphene composite material.
The titanium dioxide is in a hollow microsphere structure and is obtained by the following method: dissolving titanium potassium oxalate and nitric acid in a hydrogen peroxide solution with the mass fraction of 10% to ensure that the concentration of the titanium potassium oxalate is 500mmol/L and the concentration of the nitric acid is 0.9mmol/L to obtain a reaction solution; placing the prepared reaction solution into a reaction kettle, sealing the reaction system, and reacting for 72 hours at the constant temperature of 40 ℃; after the reaction is finished, centrifuging at 3000 r/min for 25 min, and collecting the bottom solid; the bottom solid was washed with hydrochloric acid of 0.1mol/L, which was 40 times the weight of the bottom solid, and deionized water of 100 times the weight of the bottom solid in this order, dried at 80 ℃ for 12 hours, and then treated in an air atmosphere at 450 ℃ for 1 hour.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 6 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The measured spectrum scanning curve has an absorption area of 807.4nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then pouring 10mg/L of TNT solution into a quartz culture dish, adding 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 6, standing for 24 hours in a completely dark environment, and performing uniform ultrasonic dispersion. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. Through measurement, the degradation rate of the TNT solution reaches 92.3 percent. TNT was replaced by methyl orange, and it was found that after 5 hours, the degradation rate of the aqueous solution of methyl orange reached 96.3%.
Example 7
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide/graphene composite material and 1g of selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate, 0.97g of sodium molybdate dihydrate and 0.25g of selenium powder into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; and washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the selenium-loaded bismuth molybdate.
The preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16g of sodium hydroxide into 20mL of deionized water and 20mL of glycerin, stirring for 30 minutes at 100 revolutions per minute, and then naturally cooling to 25 ℃ to prepare a sodium hydroxide aqueous solution; adding 1.4g of titanium dioxide into the aqueous solution of sodium hydroxide, and continuously stirring for 60 minutes at 100 revolutions per minute to obtain emulsion; adding 0.2g of graphene into the emulsion, stirring for 10 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 25 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 12 hours at 200 ℃; after the reaction is finished, naturally cooling the reaction system to 25 ℃, centrifuging for 20 minutes at 3000 r/min, and collecting bottom sediment to obtain a reaction product; and (3) soaking the reaction product in nitric acid with the molar concentration of 0.1mol/L for 12 hours, wherein the solid-to-liquid ratio of the reaction product to the nitric acid is 1: 40(g/L), centrifuging for 10-20 minutes at 3000 r/min, and collecting bottom solids; and washing the bottom solid with deionized water which is 230 times of the weight of the bottom solid and absolute ethyl alcohol which is 70 times of the weight of the bottom solid in sequence, and drying at 80 ℃ for 5 hours to obtain the titanium dioxide/graphene composite material.
The titanium dioxide is in a hollow microsphere structure and is obtained by the following method: dissolving titanium potassium oxalate and nitric acid in a hydrogen peroxide solution with the mass fraction of 10% to ensure that the concentration of the titanium potassium oxalate is 500mmol/L and the concentration of the nitric acid is 0.9mmol/L to obtain a reaction solution; placing the prepared reaction solution into a reaction kettle, sealing the reaction system, and reacting for 72 hours at the constant temperature of 40 ℃; after the reaction is finished, centrifuging at 3000 r/min for 25 min, and collecting the bottom solid; the bottom solid was washed with hydrochloric acid of 0.1mol/L, which was 40 times the weight of the bottom solid, and deionized water of 100 times the weight of the bottom solid in this order, dried at 80 ℃ for 12 hours, and then treated in an air atmosphere at 450 ℃ for 1 hour.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 7 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The measured spectrum scanning curve has an absorption area of 781.9nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then, 10mg/L of TNT solution is poured into a quartz culture dish, 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 7 is added, and the mixture is kept stand for 24 hours in a completely dark environment and is uniformly dispersed by ultrasonic waves. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. Through measurement, the degradation rate of the TNT solution reaches 90.2%. TNT was replaced by methyl orange, and the degradation rate of the aqueous solution of methyl orange was found to reach 94.6% after 5 hours.
Example 8
The production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide/graphene composite material and 1g of selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring at 80 rpm for 10 minutes, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance.
The preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate, 0.97g of sodium molybdate dihydrate and 0.25g of selenium powder into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; and washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the selenium-loaded bismuth molybdate.
The preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16g of sodium hydroxide into 20mL of deionized water, 10mL of ethylene glycol and 10mL of glycerin, stirring for 30 minutes at 100 revolutions per minute, and then naturally cooling to 25 ℃ to prepare a sodium hydroxide aqueous solution; adding 1.4g of titanium dioxide into the aqueous solution of sodium hydroxide, and continuously stirring for 60 minutes at 100 revolutions per minute to obtain emulsion; adding 0.2g of graphene into the emulsion, stirring for 10 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 25 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 12 hours at 200 ℃; after the reaction is finished, naturally cooling the reaction system to 25 ℃, centrifuging for 20 minutes at 3000 r/min, and collecting bottom sediment to obtain a reaction product; and (3) soaking the reaction product in nitric acid with the molar concentration of 0.1mol/L for 12 hours, wherein the solid-to-liquid ratio of the reaction product to the nitric acid is 1: 40(g/L), centrifuging for 10-20 minutes at 3000 r/min, and collecting bottom solids; and washing the bottom solid with deionized water which is 230 times of the weight of the bottom solid and absolute ethyl alcohol which is 70 times of the weight of the bottom solid in sequence, and drying at 80 ℃ for 5 hours to obtain the titanium dioxide/graphene composite material.
The titanium dioxide is in a hollow microsphere structure and is obtained by the following method: dissolving titanium potassium oxalate and nitric acid in a hydrogen peroxide solution with the mass fraction of 10% to ensure that the concentration of the titanium potassium oxalate is 500mmol/L and the concentration of the nitric acid is 0.9mmol/L to obtain a reaction solution; placing the prepared reaction solution into a reaction kettle, sealing the reaction system, and reacting for 72 hours at the constant temperature of 40 ℃; after the reaction is finished, centrifuging at 3000 r/min for 25 min, and collecting the bottom solid; the bottom solid was washed with hydrochloric acid of 0.1mol/L, which was 40 times the weight of the bottom solid, and deionized water of 100 times the weight of the bottom solid in this order, dried at 80 ℃ for 12 hours, and then treated in an air atmosphere at 450 ℃ for 1 hour.
Using a pipette to transfer 0.5mL of the photocatalyst hydrosol with high catalytic degradation performance in the embodiment 8 into a beaker, adding water to a constant volume of 400mL, carrying out ultrasonic treatment for 20 minutes, and magnetically stirring for 30 minutes at 80 rpm to obtain a solution to be detected. The absorption area of a spectral scanning curve in a spectral range of 200 to 800nm wavelength is measured by using a UV-1200 ultraviolet visible spectrophotometer (provided by Shanghai Mei spectral instruments Co., Ltd.). The absorption area of the measured spectrum scanning curve is 835.7nm2。
Adding 15mg of TNT powder into 1500mL of water to prepare a TNT solution of 10 mg/L; measuring the absorbance of the initial solution; then, 10mg/L of TNT solution is poured into a quartz culture dish, 80mL of the photocatalyst hydrosol with high catalytic degradation performance of example 8 is added, and the mixture is kept stand for 24 hours in a completely dark environment and is uniformly dispersed by ultrasonic waves. After 5 hours, a volume of TNT solution was removed and its absorbance was measured using a visible spectrophotometer. Through measurement, the degradation rate of the TNT solution reaches 95.8%. TNT was replaced by methyl orange, and it was found that after 5 hours, the degradation rate of the aqueous solution of methyl orange reached 98.1%.
From the above, the photocatalyst hydrosol with high catalytic degradation performance has good catalytic efficiency for both TNT aqueous solution and methyl orange aqueous solution. Trinitrotoluene is the main component of TNT, and ultraviolet light excites photocatalyst particles to form free electrons and holes, so that the TNT can be degraded under the excitation of visible light. surface-OH and H20 is adsorbed by the holes and oxidized to OH.radical. Meanwhile, metal ions in the water and oxygen on the surface of the titanium dioxide are reduced into metal atoms and oxygen by free electrons. Benzene rings in trinitrotoluene, the main component of TNT, are decomposed into harmless substances by OH & free radicals. Similarly, free electrons and holes formed by the photocatalyst hydrosol under the excitation action of visible light decompose nitrogen-nitrogen double bonds in methyl orange molecules to generate a photocatalytic reaction.
Compared with the prior art, the invention has the following advantages:
1. bismuth molybdate is a typical bismuth-molybdenum oxide, and is formed by bonding two functional oxides. The bismuth molybdate has a unique structure and a proper forbidden band width, and shows better catalytic activity under the irradiation of sunlight. The invention is different from the prior art that titanium dioxide is generally adopted as a carrier of the photocatalyst, and the titanium dioxide and bismuth molybdate are combined for use, so that the application range of the photocatalyst is widened, and the catalytic efficiency is enhanced.
2. Selenium and oxygen atoms have stronger bonding force, so that the surface of bismuth molybdate is greatly improved in the aspects of light absorption, electron transfer, electron hole separation and the like. The selenium-loaded bismuth molybdate replaces bismuth molybdate, so that the capability of the photocatalyst hydrosol for forming free electrons and holes under the excitation action of visible light is enhanced.
3. The graphene serving as the carbon nano material with the monoatomic layer structure has excellent electrical characteristics and is a good electron acceptor. The graphene is introduced into the field of photocatalytic degradation, and through the controllable combination with titanium dioxide, the defect of the titanium dioxide can be effectively made up, the photocatalytic property is greatly improved, the migration path of a photo-excited carrier to the surface of a material is effectively shortened, and the efficiency reduction caused by internal recombination is reduced; the ultrahigh carrier mobility of the graphene is utilized to rapidly separate electrons and holes generated by excitation, and participate in organic molecule decomposition reaction, so that the catalytic efficiency is improved.
4. The titanium dioxide with the hollow microsphere structure is combined with the porous structure and the ultrahigh specific surface area of the graphene, so that the contact area between the photocatalyst hydrosol and the degradation matrix is increased, organic molecules can be effectively adsorbed, and the photocatalytic reaction is facilitated. In addition, the graphene has certain mechanical strength, can be used as a support body, and is convenient to recycle integrally.
It should be understood that although the present description refers to embodiments, not every embodiment may contain only a single embodiment, and such description is for clarity only, and those skilled in the art will be able to make the description as a whole, and the embodiments may be appropriately combined to form other embodiments as will be appreciated by those skilled in the art.
Claims (4)
1. The production process of the photocatalyst hydrosol with high catalytic degradation performance is characterized by comprising the following steps: adding 0.2-1 g of sodium hexametaphosphate into 200-300 g of water, and stirring for 10-20 minutes to obtain a mixed solution; adding 2-6 g of titanium dioxide/graphene composite material and 1-3 g of bismuth molybdate or selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring for 5-15 minutes; then adding 2-6 g of hydrogen peroxide solution with the mass fraction of 10-20%, shearing and emulsifying for 20-40 minutes, and standing for 12-14 hours to obtain an emulsion; adding 0.2-1 g of stabilizer into the emulsion, continuously stirring for 10-20 minutes, and then adjusting the pH value to 7-8 to obtain the photocatalyst hydrosol with high catalytic degradation performance;
the preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4-5 g of bismuth nitrate pentahydrate, 0.5-1 g of sodium molybdate dihydrate and 0.2-0.5 g of selenium powder into 300-600 mL of water, stirring for 20-40 minutes, and performing ultrasonic dispersion for 10-15 minutes to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 100-300 mL of absolute ethyl alcohol, uniformly mixing, sealing the reaction system, and reacting at 150-180 ℃ for 6-12 hours; centrifuging the reaction solution, and collecting precipitate; washing the precipitate with water and absolute ethyl alcohol in sequence, and drying to obtain the selenium-loaded bismuth molybdate;
the preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16-20 g of sodium hydroxide into 10-30 mL of water and 10-30 mL of organic alcohol, stirring for 30-60 minutes, and naturally cooling to 20-30 ℃ to prepare a sodium hydroxide aqueous solution; adding 1-2 g of titanium dioxide into an aqueous solution of sodium hydroxide, and continuously stirring for 30-60 minutes to obtain an emulsion; adding 0.1-0.3 g of graphene into the emulsion, stirring for 10-30 minutes, and performing ultrasonic dispersion for 10-25 minutes to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 6-12 hours at 180-200 ℃; after the reaction is finished, naturally cooling the reaction system to 20-30 ℃, centrifuging, and collecting bottom sediment to obtain a reaction product; placing the reaction product in nitric acid with the molar concentration of 0.1-0.5 mol/L for soaking for 10-12 hours, centrifuging, and collecting bottom solids; washing the bottom solid with water and absolute ethyl alcohol in sequence, and drying to obtain a titanium dioxide/graphene composite material; the organic alcohol is ethylene glycol and glycerol, and the volume ratio of the ethylene glycol to the glycerol is (1-3): (1-3) a mixed solvent;
the titanium dioxide is in a hollow microsphere structure and is obtained by the following method: dissolving titanium potassium oxalate and nitric acid in a hydrogen peroxide solution with the mass fraction of 10-20% to ensure that the concentration of the titanium potassium oxalate is 300-600 mmol/L and the concentration of the nitric acid is 0.6-0.9 mmol/L to obtain a reaction solution; placing the prepared reaction liquid into a reaction kettle, sealing the reaction system, and reacting at the constant temperature of 40-50 ℃ for 48-72 hours; after the reaction is finished, centrifuging and collecting bottom solids; and (3) sequentially washing the bottom solid with 0.1mol/L hydrochloric acid and water respectively, drying at 60-80 ℃, and treating for 1-2 hours at 400-500 ℃ in an air atmosphere.
2. The production process of the photocatalyst hydrosol with high catalytic degradation performance as claimed in claim 1, wherein the stabilizer is one or a mixture of acetylacetone, pyruvic acid and glyoxylic acid.
3. The production process of the photocatalyst hydrosol with high catalytic degradation performance as claimed in claim 1, wherein the production process of the photocatalyst hydrosol with high catalytic degradation performance comprises the following steps: adding 1g of sodium hexametaphosphate into 200g of water, and stirring at 80 rpm for 10 minutes to obtain a mixed solution; adding 4g of titanium dioxide/graphene composite material and 1g of selenium-loaded bismuth molybdate into the mixed solution, and continuing stirring at 80 revolutions per minute for 15 minutes; then adding 6g of hydrogen peroxide solution with the mass fraction of 20%, shearing and emulsifying for 30 minutes at 5000 r/min, and standing for 12 hours to obtain an emulsion; adding 0.6g of acetylacetone into the emulsion, continuing stirring for 10 minutes at 80 r/min, and then adjusting the pH to 7 by using 1% by mass of hydrochloric acid or 1% by mass of sodium hydroxide aqueous solution to obtain the photocatalyst hydrosol with high catalytic degradation performance;
the preparation process of the selenium-loaded bismuth molybdate comprises the following steps: adding 4.85g of bismuth nitrate pentahydrate, 0.97g of sodium molybdate dihydrate and 0.25g of selenium powder into 400mL of deionized water, stirring for 30 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 15 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a dispersion liquid; then transferring the dispersion liquid into a reaction kettle, adding 200mL of absolute ethyl alcohol, uniformly mixing, sealing a reaction system, and reacting for 6 hours at 180 ℃; centrifuging the reaction solution at 2000 rpm for 10 minutes, and collecting the precipitate; washing the precipitate with deionized water 200 times the weight of the reaction product and absolute ethyl alcohol 50 times the weight of the reaction product in sequence, and drying at 60 ℃ for 10 hours to obtain the selenium-loaded bismuth molybdate;
the preparation process of the titanium dioxide/graphene composite material comprises the following steps: adding 16g of sodium hydroxide into 20mL of deionized water, 10mL of ethylene glycol and 10mL of glycerin, stirring for 30 minutes at 100 revolutions per minute, and then naturally cooling to 25 ℃ to prepare a sodium hydroxide aqueous solution; adding 1.4g of titanium dioxide into the aqueous solution of sodium hydroxide, and continuously stirring for 60 minutes at 100 revolutions per minute to obtain emulsion; adding 0.2g of graphene into the emulsion, stirring for 10 minutes at 100 revolutions per minute, and performing ultrasonic dispersion for 25 minutes under the conditions of ultrasonic power of 300W and ultrasonic frequency of 25kHz to obtain a mixed solution; pouring the mixed solution into a reaction kettle, and reacting for 12 hours at 200 ℃; after the reaction is finished, naturally cooling the reaction system to 25 ℃, centrifuging for 20 minutes at 3000 r/min, and collecting bottom sediment to obtain a reaction product; and (3) soaking the reaction product in nitric acid with the molar concentration of 0.1mol/L for 12 hours, wherein the solid-to-liquid ratio of the reaction product to the nitric acid is 1: centrifuging at 40g/L for 10-20 minutes at 3000 r/min, and collecting bottom solids; washing the bottom solid with deionized water which is 230 times of the weight of the bottom solid and absolute ethyl alcohol which is 70 times of the weight of the bottom solid in sequence, and drying at 80 ℃ for 5 hours to obtain the titanium dioxide/graphene composite material;
the titanium dioxide is in a hollow microsphere structure and is obtained by the following method: dissolving titanium potassium oxalate and nitric acid in a hydrogen peroxide solution with the mass fraction of 10% to ensure that the concentration of the titanium potassium oxalate is 500mmol/L and the concentration of the nitric acid is 0.9mmol/L to obtain a reaction solution; placing the prepared reaction solution into a reaction kettle, sealing the reaction system, and reacting for 72 hours at the constant temperature of 40 ℃; after the reaction is finished, centrifuging at 3000 r/min for 25 min, and collecting the bottom solid; the bottom solid was washed with hydrochloric acid of 0.1mol/L, which was 40 times the weight of the bottom solid, and deionized water of 100 times the weight of the bottom solid in this order, dried at 80 ℃ for 12 hours, and then treated in an air atmosphere at 450 ℃ for 1 hour.
4. The photocatalyst hydrosol with high catalytic degradation performance is characterized by being prepared by the production process of the photocatalyst hydrosol with high catalytic degradation performance according to any one of claims 1 to 3.
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