CN109248711B - Loaded TiO (titanium dioxide)2Preparation method of PPS photocatalytic film - Google Patents
Loaded TiO (titanium dioxide)2Preparation method of PPS photocatalytic film Download PDFInfo
- Publication number
- CN109248711B CN109248711B CN201811197401.5A CN201811197401A CN109248711B CN 109248711 B CN109248711 B CN 109248711B CN 201811197401 A CN201811197401 A CN 201811197401A CN 109248711 B CN109248711 B CN 109248711B
- Authority
- CN
- China
- Prior art keywords
- tio
- pps
- photocatalytic film
- precursor solution
- microporous membrane
- 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.)
- Active
Links
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 title claims abstract description 105
- 230000001699 photocatalysis Effects 0.000 title claims abstract description 94
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 title claims abstract description 46
- 238000000034 method Methods 0.000 title claims abstract description 20
- 239000004408 titanium dioxide Substances 0.000 title claims description 5
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims abstract description 66
- 239000002243 precursor Substances 0.000 claims abstract description 58
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 44
- 239000012982 microporous membrane Substances 0.000 claims abstract description 42
- 238000001027 hydrothermal synthesis Methods 0.000 claims abstract description 37
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims abstract description 23
- 239000010936 titanium Substances 0.000 claims abstract description 23
- 229910052719 titanium Inorganic materials 0.000 claims abstract description 23
- 238000003756 stirring Methods 0.000 claims abstract description 18
- 238000002360 preparation method Methods 0.000 claims abstract description 15
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims abstract description 14
- 238000001035 drying Methods 0.000 claims abstract description 14
- 229910017604 nitric acid Inorganic materials 0.000 claims abstract description 14
- 238000005406 washing Methods 0.000 claims abstract description 12
- 239000002131 composite material Substances 0.000 claims abstract description 9
- 238000011065 in-situ storage Methods 0.000 claims abstract description 6
- 238000009736 wetting Methods 0.000 claims abstract description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 38
- 238000006243 chemical reaction Methods 0.000 claims description 25
- 238000002156 mixing Methods 0.000 claims description 17
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims description 15
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims description 15
- 235000011130 ammonium sulphate Nutrition 0.000 claims description 15
- YHWCPXVTRSHPNY-UHFFFAOYSA-N butan-1-olate;titanium(4+) Chemical compound [Ti+4].CCCC[O-].CCCC[O-].CCCC[O-].CCCC[O-] YHWCPXVTRSHPNY-UHFFFAOYSA-N 0.000 claims description 7
- DCKVFVYPWDKYDN-UHFFFAOYSA-L oxygen(2-);titanium(4+);sulfate Chemical compound [O-2].[Ti+4].[O-]S([O-])(=O)=O DCKVFVYPWDKYDN-UHFFFAOYSA-L 0.000 claims description 4
- 229910000348 titanium sulfate Inorganic materials 0.000 claims description 4
- XJDNKRIXUMDJCW-UHFFFAOYSA-J titanium tetrachloride Chemical compound Cl[Ti](Cl)(Cl)Cl XJDNKRIXUMDJCW-UHFFFAOYSA-J 0.000 claims description 4
- 230000008569 process Effects 0.000 claims description 3
- VXUYXOFXAQZZMF-UHFFFAOYSA-N titanium(IV) isopropoxide Chemical compound CC(C)O[Ti](OC(C)C)(OC(C)C)OC(C)C VXUYXOFXAQZZMF-UHFFFAOYSA-N 0.000 claims description 3
- YONPGGFAJWQGJC-UHFFFAOYSA-K titanium(iii) chloride Chemical compound Cl[Ti](Cl)Cl YONPGGFAJWQGJC-UHFFFAOYSA-K 0.000 claims description 3
- MKNXBRLZBFVUPV-UHFFFAOYSA-L cyclopenta-1,3-diene;dichlorotitanium Chemical compound Cl[Ti]Cl.C=1C=C[CH-]C=1.C=1C=C[CH-]C=1 MKNXBRLZBFVUPV-UHFFFAOYSA-L 0.000 claims description 2
- 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 2
- XROWMBWRMNHXMF-UHFFFAOYSA-J titanium tetrafluoride Chemical compound [F-].[F-].[F-].[F-].[Ti+4] XROWMBWRMNHXMF-UHFFFAOYSA-J 0.000 claims description 2
- 239000002351 wastewater Substances 0.000 claims description 2
- 230000003197 catalytic effect Effects 0.000 abstract description 21
- 238000011068 loading method Methods 0.000 abstract description 19
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 abstract description 18
- 239000003054 catalyst Substances 0.000 abstract description 14
- 239000000853 adhesive Substances 0.000 abstract description 4
- 239000002105 nanoparticle Substances 0.000 abstract description 4
- 239000011148 porous material Substances 0.000 abstract description 4
- 229910021653 sulphate ion Inorganic materials 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 66
- 238000012360 testing method Methods 0.000 description 33
- 239000012528 membrane Substances 0.000 description 28
- RBTBFTRPCNLSDE-UHFFFAOYSA-N 3,7-bis(dimethylamino)phenothiazin-5-ium Chemical compound C1=CC(N(C)C)=CC2=[S+]C3=CC(N(C)C)=CC=C3N=C21 RBTBFTRPCNLSDE-UHFFFAOYSA-N 0.000 description 23
- 229960000907 methylthioninium chloride Drugs 0.000 description 23
- 239000000463 material Substances 0.000 description 15
- 239000002957 persistent organic pollutant Substances 0.000 description 15
- 239000008367 deionised water Substances 0.000 description 12
- 229910021641 deionized water Inorganic materials 0.000 description 12
- 230000004907 flux Effects 0.000 description 12
- 239000007788 liquid Substances 0.000 description 12
- 238000009991 scouring Methods 0.000 description 12
- 230000002238 attenuated effect Effects 0.000 description 11
- 239000011159 matrix material Substances 0.000 description 6
- 238000001179 sorption measurement Methods 0.000 description 4
- 230000000052 comparative effect Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 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
- 230000001070 adhesive effect Effects 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 230000007547 defect Effects 0.000 description 2
- 238000000151 deposition Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000000835 fiber Substances 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 239000002070 nanowire Substances 0.000 description 2
- 238000013033 photocatalytic degradation reaction Methods 0.000 description 2
- 239000004065 semiconductor Substances 0.000 description 2
- 238000003980 solgel method Methods 0.000 description 2
- 239000004697 Polyetherimide Substances 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
- 238000002441 X-ray diffraction Methods 0.000 description 1
- 238000004026 adhesive bonding Methods 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 230000002776 aggregation Effects 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
- 230000000844 anti-bacterial effect Effects 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 238000005266 casting Methods 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 229910000365 copper sulfate Inorganic materials 0.000 description 1
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical compound [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 238000010586 diagram 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
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 238000007210 heterogeneous catalysis Methods 0.000 description 1
- 239000012761 high-performance material Substances 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 239000013067 intermediate product Substances 0.000 description 1
- RUTXIHLAWFEWGM-UHFFFAOYSA-H iron(3+) sulfate Chemical compound [Fe+3].[Fe+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O RUTXIHLAWFEWGM-UHFFFAOYSA-H 0.000 description 1
- 229910000360 iron(III) sulfate Inorganic materials 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 235000019341 magnesium sulphate Nutrition 0.000 description 1
- 238000003760 magnetic stirring Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical class C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 1
- 239000000693 micelle Substances 0.000 description 1
- 239000004005 microsphere Substances 0.000 description 1
- 239000011943 nanocatalyst Substances 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 231100000956 nontoxicity Toxicity 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 239000002245 particle 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
- 229920001601 polyetherimide Polymers 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 229920005597 polymer membrane Polymers 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
- 239000000843 powder Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 229910052938 sodium sulfate Inorganic materials 0.000 description 1
- 235000011152 sodium sulphate Nutrition 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 238000000108 ultra-filtration Methods 0.000 description 1
Images
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
-
- 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
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/30—Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
- B01J35/39—Photocatalytic properties
-
- 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
- B01J35/00—Catalysts, in general, characterised by their form or physical properties
- B01J35/50—Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
- B01J35/58—Fabrics or filaments
- B01J35/59—Membranes
-
- 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
- C02F2101/308—Dyes; Colorants; Fluorescent agents
-
- 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
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Materials Engineering (AREA)
- Health & Medical Sciences (AREA)
- Inorganic Chemistry (AREA)
- Toxicology (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Catalysts (AREA)
- Inorganic Compounds Of Heavy Metals (AREA)
Abstract
The invention discloses a loaded TiO2The preparation method of the PPS photocatalytic film comprises the following steps: of a titanium source, sulphate with ethanol, water and hydrochloric acidMixing the composite solution, and stirring at normal temperature to be homogeneous to obtain TiO2Precursor solution; wetting a PPS microporous membrane in ethanol, and then transferring the PPS microporous membrane into a nitric acid solution with the concentration for treatment; immersing PPS microporous membrane into TiO2Transferring the precursor solution into a hydrothermal reaction kettle together for hydrothermal reaction, washing and drying to obtain PPS @ TiO2A photocatalytic film. The method adopts a high-temperature hydrothermal method to prepare TiO2Growing on the surface of the PPS microporous membrane in situ to promote TiO2The crystallinity of the nano particles can obtain the nano TiO loaded on the surface and the inner side of the pore channel with uniform pore diameter, high porosity, large specific surface area, high loading capacity, high catalyst crystallinity, firm combination and controllable appearance under the condition of avoiding using an adhesive2The PPS photocatalytic film effectively improves the specific surface area and catalytic activity of the catalyst.
Description
Technical Field
The invention belongs to the field of photocatalytic film preparation, and particularly relates to a supported TiO2The method for preparing the PPS photocatalytic film.
Background
Organic pollutants are one of the more difficult-to-treat environmental pollutants because of their stable structure and low biodegradability. The semiconductor photocatalysis technology can directly utilize light energy to completely mineralize and remove various organic pollutants, and is one of ideal organic pollutant treatment technologies. In semiconductor materials, nano TiO2Has attracted wide attention with the characteristics of high efficiency, environmental protection, no toxicity and stability. However, nano TiO2The photocatalytic material has the defects of difficult recovery, easy agglomeration and the like, and is easy to cause secondary pollution and reduce the catalytic efficiency. Therefore, the supported photocatalytic material is increasingly used.
In the research of the supported photocatalytic material, the selection of the matrix is the key of the research, and at present, the matrix mainly comprises a microsphere material, a two-dimensional material, a fiber fabric, an inorganic material and a membrane material. Among them, polymer membrane materials are receiving wide attention in terms of high porosity, high specific surface area, and strong adsorption capacity. At present, the loading modes of the supported photocatalytic material mainly include a blending method, a deposition method, a sol-gel method, an adhesive bonding method and a low-temperature hydrothermal method. The blending method needs to embed the catalyst in a polymer matrix, and limits the loading capacity and catalytic efficiency of the catalyst. The materials prepared by the deposition method and the sol-gel method have the problem of poor binding force between the catalyst and the matrix. The use of the binder not only increases the production cost, but also causes environmental pollution. The catalyst in the photocatalytic film material prepared by the low-temperature hydrothermal method exists in an amorphous form, the crystallinity is low, and the photocatalytic performance of the material is greatly reduced.
The document of application No. 201611156787.6 discloses an activated carbon fiber loaded nano TiO2A method for preparing a film. The method adopts an in-situ induced reverse micelle method to prepare the dense nano TiO with uniform loading, no crack, strong adhesive force and controllable film thickness of the activated carbon fiber2A composite photocatalytic material of film. The method effectively solves the problem of nano TiO2The photocatalytic material is difficult to recycle and easy to agglomerate, but the further application and development of the method are limited by the complex process flow, the harsh preparation conditions and the long preparation path. The document of application No. 2017111579844 discloses a surface-supported TiO2The preparation method of polyetherimide photocatalytic ultrafiltration membrane of nano wire is characterized by that it utilizes low-temp. crystallization technique to grow TiO on the surface of membrane2The nano-wire improves the hydrophilicity of the membrane, thereby improving the flux of the membrane while keeping high rejection rate, and applying the membrane to the fields of photocatalytic pollution treatment and the like. However, the catalyst has relatively limited active site exposure and the matrix has less contribution to the improvement of catalytic efficiency and has a single function.
Disclosure of Invention
Aiming at the defects of the prior art, the invention aims to solve the technical problem of providing a supported TiO2The method for preparing the PPS photocatalytic film.
The technical scheme for solving the technical problem is to provide a loaded TiO2The preparation method of the PPS photocatalytic film is characterized by comprising the following steps:
1)TiO2precursor solutionPreparing a liquid: mixing a titanium source, sulfate, ethanol, water and hydrochloric acid composite solution, and stirring at normal temperature to be homogeneous to obtain TiO2Precursor solution; TiO 22The concentration of the titanium source in the precursor solution is 1-500 g/L, and the concentration of the sulfate is 1-50 g/L; the volume ratio of the ethanol to the water to the hydrochloric acid is 2-6:1-3: 1-3;
2) pretreating a PPS microporous membrane: wetting a PPS microporous membrane in ethanol, transferring the PPS microporous membrane into a nitric acid solution with the concentration of 5-55 wt.%, and stirring for 0.5-8 hours at the temperature of 10-50 ℃;
3) high-temperature hydrothermal method for in-situ generation of PPS @ TiO2Photocatalytic film: immersing the PPS microporous membrane obtained in the step 2) into the TiO obtained in the step 1)2And transferring the precursor solution into a hydrothermal reaction kettle together for hydrothermal reaction for 2-30 h at the reaction temperature of 80-240 ℃, and washing and drying to obtain PPS @ TiO2A photocatalytic film;
adding 0.01-1 ml of TiO into each square centimeter of PPS microporous membrane2And (3) precursor solution.
Compared with the prior art, the invention has the beneficial effects that:
(1) adopts nontoxic, green, stable and antibacterial TiO2As the main catalyst, TiO is subjected to a high-temperature hydrothermal method2Growing on the surface of the PPS microporous membrane in situ to promote TiO2The crystallinity of the nano particles can obtain the nano TiO loaded on the surface and the inner side of the pore channel with uniform pore diameter, high porosity, large specific surface area, high loading capacity, high catalyst crystallinity, firm combination and controllable appearance under the condition of avoiding using an adhesive2The PPS photocatalytic film effectively improves the specific surface area and catalytic activity of the catalyst.
(2) The catalyst carrier is high-temperature-resistant, solvent-resistant and acid-alkali-corrosion-resistant high-performance material PPS, and the main chain of the PPS contains a large number of benzene rings, so that pi-type complex adsorption can be formed, the chemical adsorption of organic pollutants is improved from the perspective of a substrate, and the catalysis efficiency of the catalyst is further improved.
(3) The PPS microporous membrane has a dendritic structure, has higher specific surface area and porosity, and further improves the adsorbability of the catalytic membrane material. The improvement of the chemical adsorption is beneficial to improving the catalytic efficiency of heterogeneous catalysis, thereby obtaining the photocatalytic film with high catalytic efficiency.
(4) The introduction of the process of nitric acid pretreatment to the PPS microporous membrane can partially oxidize thioether bonds on the main chain into sulfoxide bonds to provide chemical bond binding sites on the premise of not damaging the mechanical properties of the original PPS membrane, and the sulfoxide bonds have electronegativity and can be mutually attracted with positively charged titanium source hydrolysis intermediate products to form electrostatic force binding to form firm interaction, so that the binding force of inorganic nano catalyst particles and a membrane matrix is improved, and the use of an adhesive is avoided.
(5) The preparation process is simple, the preparation flow is short, the reaction condition is mild and controllable, and the operation is convenient.
Drawings
FIG. 1 shows the TiO-supported catalyst of the present invention2SEM photograph of the photocatalytic film prepared in example 2 of the preparation method of the PPS photocatalytic film;
FIG. 2 shows the TiO loading of the present invention2The XRD pattern of the photocatalytic film prepared in the method for preparing a PPS photocatalytic film in example 2;
FIG. 3 shows the TiO loading of the present invention2The photocatalytic degradation curve diagram of the photocatalytic film prepared in the embodiment 2 of the preparation method of the PPS photocatalytic film on the methylene blue organic solvent;
FIG. 4 shows TiO loading according to the present invention2SEM photograph of the photocatalytic film prepared in comparative example 1;
Detailed Description
Specific examples of the present invention are given below. The specific examples are only intended to illustrate the invention in further detail and do not limit the scope of protection of the claims of the present application.
The invention provides a loaded TiO2The preparation method (method for short) of the PPS photocatalytic film is characterized by comprising the following steps:
1)TiO2preparing a precursor solution: mixing a titanium source, sulfate, ethanol, water and hydrochloric acid composite solution, and stirring at normal temperature to be homogeneous to obtain TiO2Precursor solution; TiO 22The concentration of the titanium source in the precursor solution is 1-500 g/L, and the concentration of the sulfate is 1-50 g/L; the volume ratio of the ethanol to the water to the hydrochloric acid is 2-6:1-3: 1-3;
preferably, the concentration of the titanium source is 10-200 g/L, the concentration of sulfate is 2-10 g/L, and the volume ratio of ethanol to water to hydrochloric acid is 3-5:1-3: 1-3;
the titanium source is at least one of tetrabutyl titanate, titanium tetrachloride, titanium sulfate, titanium trichloride, isopropyl titanate, titanocene dichloride, titanium tetrafluoride or titanium potassium oxalate;
the sulfate is at least one of ferric sulfate, ammonium sulfate, titanium sulfate, sodium sulfate, magnesium sulfate, copper sulfate, potassium sulfate or aluminum sulfate;
2) pretreating a PPS microporous membrane: wetting a PPS microporous membrane in ethanol, transferring the PPS microporous membrane into a nitric acid solution with the concentration of 5-55 wt.%, and stirring for 0.5-8 hours at the temperature of 10-50 ℃;
3) high-temperature hydrothermal method for in-situ generation of PPS @ TiO2Photocatalytic film: immersing the PPS microporous membrane obtained in the step 2) into the TiO obtained in the step 1)2And transferring the precursor solution into a hydrothermal reaction kettle together for hydrothermal reaction for 2-30 h at the reaction temperature of 80-240 ℃, washing the membrane obtained by the reaction with deionized water, and drying in an oven for 6-24 h to obtain PPS @ TiO2A photocatalytic film.
Adding 0.01-1 ml of TiO into each square centimeter of PPS microporous membrane2Precursor solution; preferably, 0.02-0.04 ml of TiO is added into each square centimeter of PPS microporous membrane2And (3) precursor solution.
PPS@TiO2The photocatalytic film can be applied to organic dye wastewater.
Example 1
1) Mixing titanium tetrachloride, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 2:1:1 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 50g/L, and the concentration of sulfate is 1 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 20% nitric acid solution and stirred at 20 ℃ for 4 hours.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 20ml of precursor solution, transferring the solution to a hydrothermal reaction kettle for hydrothermal reaction for 24 hours at the reaction temperature of 220 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 24 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 78.1% and a titania loading of 19.2%. The method for measuring the photocatalytic performance by adopting methylene blue to simulate liquid organic pollutants comprises the following specific steps: PPS @ TiO 2.5cm in diameter2Placing the photocatalytic film in 25mL of methylene blue aqueous solution (20mg/L), adsorbing for 1h under magnetic stirring in 200rmp black, then opening an ultraviolet lamp for photocatalytic degradation, and testing to obtain the PPS @ TiO2The catalytic efficiency of the photocatalytic film on methylene blue is more than 93%. Through the test of a water flow scouring test (water flow scouring for 150min under the pressure of 2 bar), the flux of the photocatalytic film is attenuated by 11 percent, and the supported TiO is2Is firm and not easy to fall off.
Example 2
1) Mixing tetrabutyl titanate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 4:1:2 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 150g/L, and the concentration of sulfate is 5 g/L;
2) the PPS microporous membrane was wetted in ethanol, and then transferred to a 10% nitric acid solution and stirred at 50 ℃ for 1 hour.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 10ml of precursor solution, transferring the precursor solution into a hydrothermal reaction kettle for hydrothermal reaction for 12 hours at the reaction temperature of 180 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 24 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 73.4% and a titania loading of 50.6%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film to methylene blue is more than 99%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 17 percent, and the loaded TiO2Is firm and not easy to fall off.
Example 3
1) Mixing titanium sulfate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 6:2:3 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of the titanium source in the precursor solution is 400g/L, and the concentration of the sulfate is 50 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 30% nitric acid solution and stirred at 20 ℃ for 1 hour.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 10ml of precursor solution, transferring the precursor solution into a hydrothermal reaction kettle for hydrothermal reaction for 30 hours at the reaction temperature of 120 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 24 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 76.8% and a titania loading of 38.7%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film to methylene blue is more than 98%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 13 percent, and the loaded TiO2Is firm and not easy to fall off.
Example 4
1) Mixing potassium titanium oxalate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 4:2:1 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 300g/L, and the concentration of sulfate is 20 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 30% nitric acid solution and stirred at 20 ℃ for 1 hour.
3) Is measured by a distance of 20cm2The obtained pretreated PPS microporous membrane is immersed in 20ml of precursor solution and transferred to a hydrothermal reaction kettle for hydrothermal reaction 1Washing the film obtained by the reaction with deionized water at the reaction temperature of 150 ℃ for 2h, and drying in an oven for 12h to obtain PPS @ TiO2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 74.6% and a titania loading of 41.4%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film to methylene blue is more than 98%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 14 percent, and the supported TiO2Is firm and not easy to fall off.
Example 5
1) Mixing isopropyl titanate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 4:1:2 at normal temperature, and stirring to be homogeneous to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 250g/L, and the concentration of sulfate is 10 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 5% nitric acid solution and stirred at 20 ℃ for 5 hours.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 10ml of precursor solution, transferring the precursor solution into a hydrothermal reaction kettle for hydrothermal reaction for 10 hours at the reaction temperature of 200 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 12 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 73.0% and a titania loading of 49.3%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film to methylene blue is more than 99%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 16 percent, and the loaded TiO2Is firm and not easy to fall off.
Example 6
1) Mixing titanium trichloride, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 6:1:2 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 100g/L, and the concentration of sulfate is 20 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 20% nitric acid solution and stirred at 30 ℃ for 2 hours.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 10ml of precursor solution, transferring the precursor solution into a hydrothermal reaction kettle for hydrothermal reaction for 24 hours at the reaction temperature of 200 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 12 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 74.2% and a titanium dioxide loading of 45.6%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film to methylene blue is more than 99%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 15 percent, and the loaded TiO2Is firm and not easy to fall off.
Example 7
1) Mixing titanium tetrachloride, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 5:2:2 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 100g/L, and the concentration of sulfate is 10 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 20% nitric acid solution and stirred at 40 ℃ for 1 hour.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 10ml of precursor solution, transferring the precursor solution into a hydrothermal reaction kettle for hydrothermal reaction for 12 hours at the reaction temperature of 180 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 12 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 76.2% and a titania loading of 33.3%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2Photocatalytic film para-methyleneThe catalytic efficiency of blue is above 98%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 15 percent, and the loaded TiO2Is firm and not easy to fall off.
Example 8
1) Mixing tetrabutyl titanate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 6:1:2 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 200g/L, and the concentration of sulfate is 10 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 25% nitric acid solution and stirred at 25 ℃ for 1 hour.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 20ml of precursor solution, transferring the solution to a hydrothermal reaction kettle for hydrothermal reaction for 12 hours at the reaction temperature of 200 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 12 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 72.7% and a titania loading of 50.1%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film to methylene blue is more than 99%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 17 percent, and the loaded TiO2Is firm and not easy to fall off.
Example 9
1) Mixing tetrabutyl titanate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 4:1:2 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 300g/L, and the concentration of sulfate is 15 g/L;
2) the PPS microporous membrane was wetted in ethanol and then transferred to a 40% nitric acid solution and stirred at 20 ℃ for 1 hour.
3) Is measured by a distance of 20cm2Immersing the obtained pretreated PPS microporous membrane into 15ml of precursor solution, transferring the precursor solution into a hydrothermal reaction kettle for hydrothermal reaction for 24 hours at the reaction temperature ofWashing the film obtained by the reaction with deionized water at 200 ℃, and drying in an oven for 12 hours to obtain PPS @ TiO2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 72.1% and a titania loading of 53.5%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film to methylene blue is more than 99%. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 18 percent, and the loaded TiO2Is firm and not easy to fall off.
Comparative example 1
1) Mixing tetrabutyl titanate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 4:1:2 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 150g/L, and the concentration of sulfate is 5 g/L;
2) is measured by a distance of 20cm2Immersing the non-pretreated PPS microporous membrane into 10ml of precursor solution, transferring the solution to a hydrothermal reaction kettle for hydrothermal reaction for 12 hours at the reaction temperature of 180 ℃, washing the membrane obtained by the reaction with deionized water, and drying the membrane in an oven for 24 hours to obtain PPS @ TiO @2A photocatalytic film.
Tested, PPS @ TiO2The photocatalytic film had a porosity of 74.6% and a titania loading of 47.8%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the photocatalytic film on methylene blue is over 88 percent. Through the test of a water flow scouring test, the flux of the photocatalytic film is attenuated by 72 percent, and the loaded TiO2The large amount of falling leads to hole blockage, and has no application value.
Comparative example 2
1) Mixing tetrabutyl titanate, ammonium sulfate, ethanol, water and hydrochloric acid at a volume ratio of 4:1:2 at room temperature, and stirring to obtain TiO2Precursor solution; TiO 22The concentration of a titanium source in the precursor solution is 150g/L, and the concentration of sulfate is 5 g/L;
2) 10ml of precursor solution was transferred toCarrying out hydrothermal reaction for 12h in a hydrothermal reaction kettle at the temperature of 180 ℃, and reacting to obtain TiO2The powder is washed clean by deionized water and dried in an oven for 24 hours to obtain TiO2And (3) nanoparticles. Will produce TiO2The nano particles are added into the casting solution according to the proportion of 5 percent by mass to prepare PPS @ TiO @2And (3) blending the composite photocatalytic film.
Tested, PPS @ TiO2The porosity of the blended composite photocatalytic film is 79.1%, and the loading rate of titanium dioxide is 5%. Adopting methylene blue to simulate liquid organic pollutants to measure photocatalytic performance, and testing to prepare PPS @ TiO2The catalytic efficiency of the blended composite photocatalytic film to methylene blue is over 71 percent. Through the test of a water flow scouring test, the flux of the blended composite photocatalytic membrane is attenuated by 8 percent, and the loaded TiO is2But the catalyst is more embedded in the membrane, so that the catalytic sites are few and the catalytic efficiency is poor.
Nothing in this specification is said to apply to the prior art.
Claims (5)
1. Loaded TiO (titanium dioxide)2The preparation method of the PPS photocatalytic film is characterized by comprising the following steps:
1)TiO2preparing a precursor solution: mixing a titanium source, ammonium sulfate, ethanol, water and hydrochloric acid composite solution, and stirring at normal temperature to be homogeneous to obtain TiO2Precursor solution; TiO 22The concentration of the titanium source in the precursor solution is 1-500 g/L, and the concentration of ammonium sulfate is 1-50 g/L; the volume ratio of the ethanol to the water to the hydrochloric acid is 2-6:1-3: 1-3;
2) pretreating a PPS microporous membrane: wetting a PPS microporous membrane in ethanol, transferring the PPS microporous membrane into a nitric acid solution with the concentration of 5-55 wt.%, and stirring for 0.5-8 hours at the temperature of 10-50 ℃;
3) high-temperature hydrothermal method for in-situ generation of PPS @ TiO2Photocatalytic film: immersing the PPS microporous membrane obtained in the step 2) into the TiO obtained in the step 1)2And transferring the precursor solution into a hydrothermal reaction kettle together for hydrothermal reaction for 2-30 h at the reaction temperature of 80-240 ℃, and washing and drying to obtain PPS @ TiO2A photocatalytic film;
adding 0.01-1 ml of TiO into each square centimeter of PPS microporous membrane2And (3) precursor solution.
2. The TiO-supported according to claim 12The preparation method of the PPS photocatalytic film is characterized in that the concentration of a titanium source is 10-200 g/L, the concentration of ammonium sulfate is 2-10 g/L, and the volume ratio of ethanol to water to hydrochloric acid is 3-5:1-3: 1-3.
3. The TiO-supported according to claim 12The preparation method of the PPS photocatalytic film is characterized in that the titanium source is at least one of tetrabutyl titanate, titanium tetrachloride, titanium sulfate, titanium trichloride, isopropyl titanate, titanocene dichloride, titanium tetrafluoride or titanium potassium oxalate.
4. The TiO-supported according to claim 12The preparation method of the PPS photocatalytic film is characterized in that 0.02-0.04 ml of TiO is added into each square centimeter of PPS microporous film2And (3) precursor solution.
5. PPS @ TiO obtainable by the process according to any one of claims 1 to 42The application of the photocatalytic film in organic dye wastewater.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811197401.5A CN109248711B (en) | 2018-10-15 | 2018-10-15 | Loaded TiO (titanium dioxide)2Preparation method of PPS photocatalytic film |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811197401.5A CN109248711B (en) | 2018-10-15 | 2018-10-15 | Loaded TiO (titanium dioxide)2Preparation method of PPS photocatalytic film |
Publications (2)
Publication Number | Publication Date |
---|---|
CN109248711A CN109248711A (en) | 2019-01-22 |
CN109248711B true CN109248711B (en) | 2021-08-13 |
Family
ID=65046352
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201811197401.5A Active CN109248711B (en) | 2018-10-15 | 2018-10-15 | Loaded TiO (titanium dioxide)2Preparation method of PPS photocatalytic film |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109248711B (en) |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110694604B (en) * | 2019-10-11 | 2023-09-12 | 巨鹏(肇庆)信息科技有限公司 | TiO (titanium dioxide) 2 PPy super-infiltration photocatalytic composite material and preparation method thereof |
CN110860218B (en) * | 2019-12-15 | 2021-11-30 | 天津工业大学 | Preparation method of PAN-based oil-water separation microporous membrane with photocatalytic function |
CN112295421B (en) * | 2020-10-20 | 2022-11-15 | 天津理工大学 | Surface-bonded TiO2/PVDF ultrafiltration membrane for photocatalysis |
CN112411177B (en) * | 2020-10-27 | 2022-08-12 | 深圳市铁汉人居环境科技有限公司 | Fiber comprising titanium dioxide nanostructure, preparation method and fabric |
CN113713627A (en) * | 2021-08-13 | 2021-11-30 | 清华大学 | Ceramic ultrafiltration membrane with catalytic function and preparation method and application thereof |
CN114162912B (en) * | 2021-11-04 | 2023-09-26 | 泉州南京大学环保产业研究院 | Preparation method of high {001} crystal face-loaded titanium dioxide particle electrode |
CN114534494B (en) * | 2022-03-07 | 2023-03-31 | 四川轻化工大学 | Ultrafiltration membrane with photocatalytic activity and preparation method and application thereof |
Family Cites Families (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE19916468C1 (en) * | 1999-04-12 | 2000-12-21 | Ticona Gmbh | Rapid oxidation of polyarylene sulfide fiber material |
CN1156336C (en) * | 2002-07-12 | 2004-07-07 | 清华大学 | Preparation method of titanium dioxide film photocatalyst loaded on surface of flexible base material |
JP5131638B2 (en) * | 2008-05-27 | 2013-01-30 | 信越化学工業株式会社 | Production method of titanium oxide photocatalyst thin film |
CN101735613B (en) * | 2009-12-08 | 2012-09-05 | 四川大学 | Porous polymer nanoparticle and preparation method thereof |
CN102145241B (en) * | 2011-02-18 | 2013-02-27 | 福州大学 | Preparation method of denitration-catalyst-supported polyphenylene sulfide (PPS) filter material |
CN102512878B (en) * | 2011-12-28 | 2013-10-09 | 南京际华三五二一特种装备有限公司 | Dust removal and waste gas decomposition double-effect filter material and preparation method thereof |
US20140144834A1 (en) * | 2012-11-29 | 2014-05-29 | Seok Won Hong | Membrane with titanium dioxide nanostructure and method for fabricating the same |
CN104258852B (en) * | 2014-10-23 | 2016-08-24 | 河海大学 | The multi-layer porous photocatalysis film of titanium dioxide of modified by silver, Its Preparation Method And Use |
CN104894680B (en) * | 2015-06-15 | 2017-03-01 | 东华大学 | A kind of PPS/ Graphene hybridization compounding fiber and preparation method thereof |
CN106215727B (en) * | 2016-08-14 | 2018-09-11 | 太原市晋华恒远科技有限公司 | A kind of preparation method of polyaminoacid modified polyphenyl thioether perforated membrane |
CN106674568B (en) * | 2016-12-06 | 2019-11-26 | 上海锦湖日丽塑料有限公司 | It is a kind of with visible light-responded automatically cleaning ABS sheet material and preparation method thereof |
CN106731226B (en) * | 2016-12-09 | 2018-11-27 | 福州大学 | The method that one step in-situ synthesis prepares binary denitration sulfur resistant catalyst load filtrate |
CN108211813B (en) * | 2018-02-12 | 2020-12-22 | 天津工业大学 | Has GO/TiO2PPS microporous membrane of additive and low-temperature denitration catalytic membrane |
-
2018
- 2018-10-15 CN CN201811197401.5A patent/CN109248711B/en active Active
Also Published As
Publication number | Publication date |
---|---|
CN109248711A (en) | 2019-01-22 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN109248711B (en) | Loaded TiO (titanium dioxide)2Preparation method of PPS photocatalytic film | |
Peng et al. | Advanced MOFs@ aerogel composites: construction and application towards environmental remediation | |
Cai et al. | Soft BiOBr@ TiO 2 nanofibrous membranes with hierarchical heterostructures as efficient and recyclable visible-light photocatalysts | |
CN109759114B (en) | g-C3N4/TiO2RGO three-dimensional Z-shaped photocatalyst and in-situ electrospinning preparation method thereof | |
CN110078126B (en) | Immobilized tungsten trioxide nano materials with different shapes and preparation method and application thereof | |
CN107252696B (en) | A kind of preparation method of sisal hemp carbon fiber photochemical catalyst | |
CN105463828B (en) | A kind of method of the carried titanium dioxide nano wire on dacron | |
Wang et al. | Ag@ AgCl nanoparticles in-situ deposited cellulose acetate/silk fibroin composite film for photocatalytic and antibacterial applications | |
CN111111777B (en) | Preparation method of Pd-based polydopamine-coated carbon nanotube catalyst and application of Pd-based polydopamine-coated carbon nanotube catalyst in Heck reaction | |
CN109046450B (en) | BiOCl/(BiO)2CO3Preparation method and application of loaded cellulose acetate/fibroin hybrid membrane | |
KR20140135306A (en) | Crystalline Iridium Oxide Nanoparticles Decorated on the One Dimensional Metal Oxide Nano-fibers as Water Oxidation Catalyst and Fabrication Method for Preparing the Same | |
CN105107477A (en) | Hyperbranched polymer/clay mineral hybrid material and preparation method thereof | |
CN112206826B (en) | Preparation method and application of cobalt-iron alloy magnetic chitosan carbonized microsphere | |
CN111111638B (en) | Preparation method of fly ash photocatalytic material | |
CN102233267A (en) | Integrated photocatalyst and preparation method thereof | |
CN111318305B (en) | Non-noble metal bifunctional catalyst and preparation method and application thereof | |
Hao et al. | Integration of g-C3N4 into cellulose/graphene oxide foams for efficient photocatalytic Cr (VI) reduction | |
Zhao et al. | Enhancing corrosion inhibition performance of ZnO solid solution by doping variable-valence rare-earth element cerium | |
CN115715990B (en) | g-C 3 N 4 vermiculite/TiO 2 Preparation method and application of ternary composite material | |
CN101157807A (en) | Method for preparing nano ZnS coated carbon nano-tube | |
CN115282792B (en) | Preparation method of polymer-magnetic organic metal framework compound composite separation membrane | |
CN116850796A (en) | Super-hydrophilic photocatalytic self-cleaning ceramic composite membrane and preparation method and application thereof | |
CN109482191B (en) | Foamed nickel loaded zinc titanate/tourmaline photocatalytic material and preparation method thereof | |
CN111185152A (en) | Multifunctional coupled PAC/Bi2O3/TiO2Method for preparing composite material | |
CN115644174A (en) | Silver/graphite alkyne composite material and preparation method and application thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |