CN1887416A - Microwave process and application of foamed nickel supported and modified nanometer TiO2 - Google Patents

Microwave process and application of foamed nickel supported and modified nanometer TiO2 Download PDF

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Publication number
CN1887416A
CN1887416A CN 200610085775 CN200610085775A CN1887416A CN 1887416 A CN1887416 A CN 1887416A CN 200610085775 CN200610085775 CN 200610085775 CN 200610085775 A CN200610085775 A CN 200610085775A CN 1887416 A CN1887416 A CN 1887416A
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China
Prior art keywords
tio
photocatalyst
sol
foamed nickel
preparation
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丁震
陈晓东
陈连生
林萍
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JIANGSU DISEASE PREVENTION CONTROL CENTRAL
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JIANGSU DISEASE PREVENTION CONTROL CENTRAL
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Abstract

The present invention discloses microwave heating process for preparing nanometer TiO2 photocatalyst, and the nanometer TiO2 photocatalyst is modified through mixing metal ion and supported with foamed nickel when used in degrading formaldehyde gas and volatile organic matter. Transparent TiO2 sol is prepared through hydrolyzing organic titanium precursor with alkoxyl titanium or through treating inorganic titanium precursor in a coprecipitation-peptization process, and during the preparation, AgNO3 and La(NO3)3 .nH2O in different ratios are added. After loaded on foamed nickel plate as carrier, the TiO2 sol is calcined at 250 deg.c under air atmosphere inside a muffle furnace for 1 hr to obtain foamed nickel plate with supported modified nanometer TiO2 photocatalyst. The present invention has high photocatalysis efficiency, and may be used in degrading formaldehyde gas and volatile organic matter in the air effectively.

Description

Microwave preparation of foamed nickel loaded modified nano TiO2Method and application of
Technical Field
The invention belongs to the fields of chemistry and chemical engineering and environmental protection, and particularly relates to a method for loading modified nano TiO on metal foam nickel by using microwaves2The preparation method of the photocatalyst can effectively remove the pollution of formaldehyde and volatile organic pollutants (VOCs) in indoor air.
Background
The discovery of nano TiO in 19722Since the photocatalysis phenomenon, the nano photocatalysis technology is developed rapidly, and has the advantages of mild reaction conditions, low energy consumption, less secondary pollution, capability of oxidizing and decomposing organic matters with stable structures at normal temperature and normal pressure, and the like. The heterogeneous photocatalytic oxidation technology has been attracting attention of researchers. Research in recent years shows that many organic pollutants which are difficult to degrade, such as halogenated hydrocarbons, organic phosphorus compounds, pesticides, surfactants, organic dyes and the like, can obtain obvious degradation effect under the photocatalytic oxidation effect. Current research indicates that the compounds are useful as photocatalytic semiconductors (including TiO)2、ZnO、CdS、PbS、WO3、MoO3And SnO2) The catalytic ability of (2) is related to its energy level structure, and in general, the larger the forbidden band width, the stronger the catalytic oxidation ability. From the viewpoint of forbidden energy level, the photocatalytic activity sequence of these above conventional semiconductor materials is TiO2>ZnO>WO3Due to TiO2Has the advantages of strong oxidation-reduction property, good chemical property stability, no secondary pollution, no toxicity, indissolvability, safety, low cost and the like, and is one of green and environment-friendly catalysts with development prospect, so that the TiO is2The photocatalytic oxidation technology has great application potential.
The current research is focused on the reduction of nano TiO by treatment during the preparation phase2Grain size of the crystal grains, increasing TiO2Increasing the degree of lattice distortion and expansion of TiO2The photocatalytic efficiency of the photocatalyst; on the other hand, nano TiO2The photocatalyst is supported on different carrier materials to obtain higher photocatalytic efficiency, and the commercial TiO is prepared by Fumihide in Japan2Loaded on honeycomb ceramic material and matched with activated carbon for useDegradation of Formaldehyde gas (Chem Eng Sci, 2003, 58 (6): 929), Ichiura uses textile printing technology to deposit TiO2Supported on zeolite flakes degrades organic contaminants (chemisphere, 2003, 50 (5): 673), but these materials act as a support for liability and lower photocatalytic efficiency due to the low amount of photocatalyst that is not highly porous.
Through the search of the prior patent documents, the following results are found: chinese patent: CN 1394675A discloses a flexible substrate material surface loaded with TiO2A process for preparing the film photocatalyst includes such steps as preparing the sol of active layer from n-butyl titanate or titanium tetrachloride as precursor, adding pore-forming agent, coating the sol of active layer on the cleaned flexible substrate, centrifugal removing excess sol, loading the flexible substrate in hydrothermal reactor, and low-temp preparing nano-class TiO by using water-alcohol as mixed solvent2A thin film photocatalyst. Chinese patent: CN 1712131A discloses a foam metal loaded TiO2The preparation method of the nanometer photocatalysis net is characterized in that a foam metal sheet is used as a carrier, before a photocatalysis active component is loaded, an inert material is loaded on the foam metal sheet to be used as a transition intermediate layer, then the foam metal sheet is impregnated with sol which uses tetrabutyl titanate or titanium tetrachloride or titanium trichloride as a precursor, and the supported photocatalysis net is prepared through drying and calcining.
So far, the application of microwave heating technology to nano TiO has not been searched2Research report on preparation process of photocatalystAnd (4) carrying out the following steps.
Disclosure of Invention
The invention provides a metal foam nickel loaded nanometer TiO2Method for preparing photocatalyst, and method for preparing metal ion-doped TiO by hydrolysis of alkoxy titanium and chemical coprecipitation2Sol, heating and calcining at lower temperature by using a microwave muffle furnace to prepare TiO loaded on the surface of the foamed nickel2The film, the carrier material has high removal efficiency on typical organic pollutants of formaldehyde and Volatile Organic Compounds (VOCs) caused by indoor air decoration, and the specific preparation stepsComprises the following steps:
1.TiO2preparation of the Sol
TiO of the invention2The sol is prepared by two methods respectively: a hydrolysis method of alkoxy titanium by taking organic titanium as a precursor and a chemical coprecipitation-peptization method by taking inorganic titanium salt as a precursor.
With tetra-n-butyl titanate [ Ti (OC)4H9)4]Preparing pure TiO by hydrolysis of alkoxy titanium as precursor2Sol and TiO modified by Fe, Ag and La ions2And (3) sol. The alkoxy hydrolysis method is characterized in that titanium alkoxide (titanate) is used as a raw material, anhydrous low-carbon alcohol (ethanol, n-butyl alcohol and isopropanol) is used as an organic solvent, and the raw material and a certain amount of acidified water are hydrolyzed together. The method adopts inorganic strong acid for catalysis, and a small amount of titanium alkoxide-alcohol solution is dripped into a large amount of water, so that the titanium alkoxide is fully hydrolyzed in an excessive water medium to generate [ Ti (OH)6]2-The ions and the hydrolysate are controlled in an acidic condition, the generated nucleating particles have positive charges, and the dispersed particles are mutually repelled due to the action of an electric double layer, so that stable TiO can be finally formed2A hydrosol.
The hydrolysis and polycondensation reaction of butyl titanate is as follows:
chemical coprecipitation-peptization method for preparing TiO2Is characterized in that cheap inorganic titanium source TiCl can beused4(or titanium disulfide) is used as a starting material, and the reaction condition is mild and is basically carried out under the conditions of normal temperature and normal pressure. TiCl can be inhibited by mainly controlling the reaction temperature and pH value4And then Ti (OH)4The precipitation rate of (a), which directly affects the particle size and stability of the sol system; the peptization aging process will directly affect the crystal structure integrity of the sol nanoparticles.
The reaction equation is as follows:
(light yellow solution)
(white precipitate)
(acid clear Sol)
(Sol particles crystallized by oxygen bridge combination)
(neutral transparent Sol)
2. Carrier pretreatment and coating method
Ultrasonically cleaning a foamed nickel plate in ethanol for 15min, drying in a constant-temperature air-blast drying oven, and soaking in the prepared TiO2In the sol, a soaking-pulling method is adopted to plate a film on the foamed nickel, the film is pulled at the speed of 5mm/s, and after the film is completely pulled, the film is dried in a blast drying oven for 15min at the temperature of 80 ℃, and the process is repeated for 2 times.
3. Putting the dried and coated foam nickel plate into an American PHOENIX microwave muffle furnace, calcining for 1h at the temperature rising rate of 30 ℃/min at the temperature of 250 ℃ in air atmosphere to prepare the supported nano TiO2A thin film nickel foam sheet.
4. The photocatalysis effect experiment is carried out in the experiment chamber, and the specification of the experiment chamber is as follows: 30cm x 30cm, 27L volume of organic glass cabin lined with polytetrafluoroethylene, photocatalytic reactor placed in the cabin: a cubic glass box with a square cross section, a side length of 8cm and a length of 20cm, wherein one end of the cubic glass box is provided with a fan, and 2 loaded nano TiO chips are obliquely inserted in the middle2The foamed nickel of the photocatalyst is added with an ultraviolet lamp tube (power 13W, characteristic wavelength 254nm, ultraviolet light intensity 19.85 mw/cm) in the middle of a 2-layer plate2). A certain amount of formaldehyde and volatile organic gases were generated in the chamber, respectively, and the experiment was conducted for 90min, and the change in the concentration of pollutants in the chamber was tested using a uk ppm400 formaldehyde tester and a us PGM-7240 VOCs tester.
Drawings
FIG. 1 shows TiO of the present invention2Transmission Electron Microscopy (TEM) and electron diffraction patterns of the sol;
FIG. 2 shows the preparation of lanthanum-doped 1.5% TiO using microwave in accordance with the present invention2Transmission Electron Microscope (TEM) and electron diffraction patterns of the powder;
FIG. 3 shows the preparation of lanthanum-doped 1.5% TiO using microwave in accordance with the present invention2X-ray diffraction (XRD) pattern of the powder;
FIG. 4 shows the loading of lanthanum-doped 1.5% TiO prepared by microwave according to the invention2Scanning photographs (SEM) and energy spectrum analysis (XPS) of the foamed nickel surface.
Detailed Description
Example 1:
1. adding 25mL of butyl titanate into 8mL of isopropanol, and fully and uniformly mixing; preparing 200mL deionized water solution containing 2mL and 70 wt% nitric acid, and adding silver nitrate (AgNO) into dilute nitric acid solution3]Wherein the mass ratio of Ag to Ti is 1.5%, adding 0.5mL of acetylacetone chelating agent and 1.Og of polyethylene glycol (PEG1500) organic polymer; slowly dripping the organic alcohol titanium acid mixed solution into the aqueous solution at the speed of 1 drop per second under the condition of high-speed stirring, and simultaneously controlling the temperature of the reaction solution to be about 70 ℃ by using a constant-temperature water bath until the butyl titanate is completely hydrolyzed. Adjusting the pH value to 3, continuously stirring for 12h, peptizing at room temperature and aging for 24h to finally form transparent TiO2And (3) sol.
2 pieces of metal foam nickel plates which are ultrasonically cleaned by ethanol are soaked in the prepared TiO2Pulling the sol at a speed of 5mm/s, taking out, drying in a forced air drying oven at 80 ℃ for 15min, repeating the process for 2 times, putting the dried and coated foam nickel plate into an American PHOENIX microwave muffle furnace, calcining at the temperature of 250 ℃ in air atmosphere at the temperature of 30 ℃/min for 1h to obtain the loaded nano TiO2A thin film nickel foam sheet.
The prepared loaded nano TiO is used in an experimental cabin2Photocatalytic degradation of formaldehyde and Volatile Organic Compounds (VOCs) by using foamed nickel plate of photocatalystThe test is carried out for 90min, and the initial concentration of the generated formaldehyde gas is 1.03mg/m3After 90min of reaction, the first part is removedThe aldehyde concentration was 0.14mg/m3The degradation rate is 89%; initial concentration of VOCs 4.05mg/m occurs3The concentration of VOCs after 90min of reaction is 0.76mg/m3And the degradation rate is 85 percent.
Example 2:
with the same TiO as in example 12The sol preparation process is characterized by adding lanthanum nitrate La (NO) into dilute nitric acid water solution3)3·nH2O]Wherein the La/Ti mass ratio is 1.0 percent, and the photocatalytic degradation experiment is also carried out to obtain the formaldehyde concentration of 0.12mg/m after the reaction is carried out for 90min3The degradation rate is 89%; initial concentration of VOCs 4.04mg/m occurs3The concentration of VOCs after 90min of reaction is 0.82mg/m3And the degradation rate is 80 percent.
Example 3:
with the same TiO as in example 12The sol preparation process is characterized by adding lanthanum nitrate La (NO) into dilute nitric acid water solution3)3·nH2O]Wherein the La/Ti mass ratio is 1.5 percent, and the photocatalytic degradation experiment is also carried out to obtain the formaldehyde concentration of 0.06mg/m after the reaction is carried out for 90min3The degradation rate is 94%; initial concentration of VOCs 4.08mg/m occurs3The concentration of VOCs after 90min of reaction is 0.54mg/m3And the degradation rate is 87 percent.
Example 4:
50mL of TiCl was taken4Dropwise adding the mixture into 100mL of deionized water at 5 ℃, and adding lanthanum nitrate [ La (NO) into the water3)3·nH2O]Wherein the La/Ti mass ratio is 1.5%, stirring at high speed while adjusting TiCl4The dropping speed of the liquid is controlled by using an ice water bath to control the temperature of the reaction liquid to be 50-60 ℃ until a light yellow transparent liquid is formed. To ensure TiCl4The hydrolysis reaction is completed, and 10 percent ammonia water diluted solution is slowly dripped into the TiCl4Fully stirring the hydrolysate, and finally adjusting the pH value to 10.0 to finally form white precipitate. For removing inorganic salt ammonium ion (NH)4 +) And chloride ion (Cl)-) Washing the precipitate with deionized water, suction filtering, and reactionWashing for several times until the pH value of the filtrate is lower than 7.5; dispersing the precipitate in deionized water to form suspension system, regulating pH of water dispersion phase to 1.5 with 10% hydrochloric acid or nitric acid solution, stirring at room temperature for 12 hr, aging for 24 hr to obtain uniform and transparent TiO2And (4) diluting the sol.
2 pieces of metal foam nickel plates which are ultrasonically cleaned by ethanol are soaked in the prepared TiO2Pulling the sol at a speed of 5mm/s, taking out, drying in a forced air drying oven at 80 ℃ for 15min, repeating the process for 2 times, putting the dried and coated foam nickel plate into an American PHOENIX microwave muffle furnace, calcining at the temperature of 250 ℃ in air atmosphere at the temperature of 30 ℃/min for 1h to obtain the loaded nano TiO2A thin film nickel foam sheet.
The prepared loaded nano TiO is used in an experimental cabin2The foam nickel plate of the photocatalyst is subjected to an experiment of photocatalytic degradation of formaldehyde and Volatile Organic Compounds (VOCs) for 90min, and the initial concentration of generated formaldehyde gas is 1.02mg/m3The concentration of formaldehyde after 90min of reaction is 0.08mg/m3The degradation rate is 92 percent; initial concentration of VOCs 4.11mg/m occurs3The concentration of VOCs after 90min of reaction is 0.61mg/m3And the degradation rate is 85 percent.

Claims (3)

1. Metallic foam nickel loaded nano TiO2The preparation method of the photocatalyst is characterized in that the metal ion-doped TiO is prepared by alkoxy titanium hydrolysis method and chemical coprecipitation method2Sol is catalyzed by inorganic strong acid, the reaction temperature is controlled at 60-70 ℃, and TiO is loaded by microwave heat treatment2Foamed nickel plate of photocatalyst.
2. The modified nano TiO for treating formaldehyde gas and Volatile Organic Compounds (VOCs) according to claim 12The preparation method of the photocatalyst is characterized in that the optimal doped metal ion is La3+The optimum doping ratio is 1.5% (La/Ti mass ratio).
3. The method of claim 1Of nano TiO2The preparation method of the photocatalyst is characterized in that the supported nano TiO is heated and treated by a microwave muffle furnace2The temperature rise rate of the foam nickel plate of the photocatalyst is 30 ℃/min, and the foam nickel plate is calcined for 1h at the temperature of 250 ℃ in the air atmosphere.
CN 200610085775 2006-06-30 2006-06-30 Microwave process and application of foamed nickel supported and modified nanometer TiO2 Pending CN1887416A (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103586041A (en) * 2013-09-01 2014-02-19 长沙理工大学 Vanadium pentoxide/titanium dioxide composite photocatalyst for degrading formaldehyde
CN106757374A (en) * 2016-12-27 2017-05-31 重庆中鼎三正科技有限公司 A kind of method of use TiO 2 sol deposition of titanium oxide whisker
CN107983365A (en) * 2017-12-15 2018-05-04 江苏龙净科杰催化剂再生有限公司 Using titanium foam as VOCs catalyst of carrier and preparation method thereof
CN112604676A (en) * 2020-11-19 2021-04-06 江苏海普功能材料有限公司 Doped visible light catalytic net and preparation method thereof
CN116212950A (en) * 2021-12-02 2023-06-06 惠生工程(中国)有限公司 Metal porous heat-conducting catalyst system and method for preparing glycolide at low temperature and low pressure

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103586041A (en) * 2013-09-01 2014-02-19 长沙理工大学 Vanadium pentoxide/titanium dioxide composite photocatalyst for degrading formaldehyde
CN103586041B (en) * 2013-09-01 2016-03-16 长沙理工大学 A kind of photochemical catalyst of vanadic anhydride composite titanium dioxide of degradation of formaldehyde
CN106757374A (en) * 2016-12-27 2017-05-31 重庆中鼎三正科技有限公司 A kind of method of use TiO 2 sol deposition of titanium oxide whisker
CN107983365A (en) * 2017-12-15 2018-05-04 江苏龙净科杰催化剂再生有限公司 Using titanium foam as VOCs catalyst of carrier and preparation method thereof
CN107983365B (en) * 2017-12-15 2020-08-07 江苏龙净科杰环保技术有限公司 VOCs catalyst with titanium foam as carrier and preparation method thereof
CN112604676A (en) * 2020-11-19 2021-04-06 江苏海普功能材料有限公司 Doped visible light catalytic net and preparation method thereof
CN116212950A (en) * 2021-12-02 2023-06-06 惠生工程(中国)有限公司 Metal porous heat-conducting catalyst system and method for preparing glycolide at low temperature and low pressure

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