CN109999888A - The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the application for toluene of degrading - Google Patents

The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the application for toluene of degrading Download PDF

Info

Publication number
CN109999888A
CN109999888A CN201910369618.8A CN201910369618A CN109999888A CN 109999888 A CN109999888 A CN 109999888A CN 201910369618 A CN201910369618 A CN 201910369618A CN 109999888 A CN109999888 A CN 109999888A
Authority
CN
China
Prior art keywords
tio
copper
nitrogen
solution
titanium dioxide
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.)
Pending
Application number
CN201910369618.8A
Other languages
Chinese (zh)
Inventor
佘厚德
马晓玉
王龙龙
李良善
苏碧桃
王其召
王磊
黄静伟
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Northwest Normal University
Original Assignee
Northwest Normal University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Northwest Normal University filed Critical Northwest Normal University
Priority to CN201910369618.8A priority Critical patent/CN109999888A/en
Publication of CN109999888A publication Critical patent/CN109999888A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/24Nitrogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Catalysts (AREA)

Abstract

The invention discloses the preparation of a kind of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the applications for toluene of degrading, and are mixed in order by dehydrated alcohol, copper nitrate, butyl titanate and glacial acetic acid, are stirred evenly, obtain solution A;Urea is dissolved in deionized water, obtains B solution;B solution instills solution A, is uniformly mixing to obtain Cu-N-TiO2Colloidal sol, it is dry after ageing, it grinds, copper and nitrogen co-doped modified titanium dioxide photocatalyst is made in roasting.Photochemical catalyst obtained is for explaining toluene.Copper and nitrogen are successfully doped in titanium dioxide by preparation method of the present invention using simple sol-gel method, have been expanded the visible light light absorption range of titanium dioxide, have been increased the utilization rate to sunlight.Photochemical catalyst obtained is used in the reaction of Photocatalytic Degradation of Toluene, is compared to pure titanium oxide and is only adulterated Cu or N, copper and nitrogen co-doped modified titanic oxide degradation of toluene rate with higher, has reached 38%.

Description

The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and toluene of degrading Using
Technical field
The invention belongs to nanocomposite technical fields, are related to a kind of Cu and N codope modification TiO2Photochemical catalyst Preparation;The photochemical catalyst is mainly used in the photocatalytic degradation reaction of toluene.
Background technique
Volatile organic matter (VOC) is one of main gaseous contamination source in environment, and Long Term Contact can cause human body sternly The harm of weight.And toluene is common one of volatile organic compounds, usually mainly as solvent or diluent for painting, rubber, In the industries such as leather, printing, insulating materials.If human body is chronically in the environment of a certain concentration toluene, will cause in chronic Poison leads to encephalopathy and hepatorenal damage, or even has carcinogenesis.Currently, mainly by photochemical catalytic oxidation, chemical oxidation, burning and VOC in the non-destructive methods control environment such as the disruptive methods such as biofiltration and absorption, absorption and film filtering.In recent years Come, photocatalysis technology is widely used in removal organic polluter because of the features such as reaction condition is mild, secondary pollution is small.Ultraviolet Or under the irradiation of visible light, photochemical catalyst generates electrons and holes and is further converted to hydroxyl radical free radical (OH), superoxide anion (•O2 ) isoreactivity group.VOCs can be aoxidized by these active groups and be generated CO2、H2O and other inorganic molecules.Therefore, light Catalysis technique is the technology for solving the problems, such as the most development potentiality of organic contamination.
Titanium dioxide (TiO2) it is a kind of excellent conductor photocatalysis material.With nontoxic, chemical property is relatively stable, Catalytic activity is high, oxidability is strong, it is cheap, can reuse, can be CO by organic pollutant degradation2、H2O etc. is nontoxic The advantages that oxide is the environmental type photochemical catalyst of current most development prospect.However, TiO2Forbidden band it is wider (3.2eV), absorption spectrum ranges are relatively narrow, only in response to ultraviolet light;Secondly, TiO2Internal and surface light induced electron has with hole High recombination rate, results in TiO2Photocatalysis degradation organic contaminant performance it is lower.Therefore, light induced electron and hole are reduced Recombination rate and expansion become TiO in the optical response range of visible light region2The Main way of Photocatalyst.Currently, TiO2 Doping with element has proved to be effectively by spectral response from the ultraviolet method for expanding to visible light-responded range, effectively drops The recombination rate of low light induced electron and hole.For example, N adulterates TiO2Visible light-responded range can be widened, this is because N2p and Interaction between O2p track, results in TiO2Valence band location move up.Ag adulterates TiO2Photoproduction can be significantly improved Electron transport ability reduces the recombination rate in light induced electron and hole, improves the catalytic activity of photochemical catalyst.
Summary of the invention
The object of the present invention is to provide the preparation methods of a kind of copper and nitrogen co-doped modified titanium dioxide photocatalyst, are made Cu-N-T iO2Nano material.
It is a further object to provide nano materials made from a kind of above-mentioned preparation method to drop as photocatalysis Solve the application in toluene.
To achieve the above object, the technical scheme adopted by the invention is that: a kind of copper and nitrogen co-doped modified titanic oxide The preparation method of photochemical catalyst, specifically sequentially includes the following steps:
1) 1 ︰, 8~10 ︰ 2~3 by volume takes butyl titanate, dehydrated alcohol and glacial acetic acid respectively, then presses four fourth of 5mL metatitanic acid The ratio of 0.06~0.08g copper nitrate is added in ester, takes copper nitrate;Urea, the quality of taken urea and taken copper nitrate are taken again Than for 4~6 ︰ 1;
Dehydrated alcohol, copper nitrate, butyl titanate and glacial acetic acid are mixed in order, it is molten to obtain A by 30~50 min of magnetic agitation Liquid;
Taken urea is dissolved completely in deionized water, is stirred evenly, B solution is obtained;
2) B solution is slowly dropped into solution A, stirs 2~3 h, obtains Cu-N-TiO2Colloidal sol;
3) by Cu-N-TiO2After colloidal sol is aged 22~24 h, in 80 DEG C~100 DEG C of at a temperature of 10~12h of drying, after grinding, In 500 DEG C~550 DEG C of 2~4h of roasting temperature, copper and nitrogen co-doped modified titanium dioxide photocatalyst (Cu-N- is made TiO2Nano material).
Another technical solution of the present invention is: a kind of above-mentioned copper and nitrogen co-doped modified titanic oxide photocatalysis Application of the agent in Photocatalytic Degradation of Toluene.
Preparation method of the present invention is successfully prepared Cu-N-TiO using simple sol-gel method2Photochemical catalyst, and by its Visible light photocatalytic degradation for toluene.Photochemical catalyst is characterized using technologies such as XRD, SEM, UV-vis and PL.It is right Material has carried out the performance test of Photocatalytic Degradation of Toluene, and excellent Photocatalytic Degradation Property is shown by test result, This has a very important significance the research and application of semiconductor light-catalyst.
Detailed description of the invention
Fig. 1 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The scanning electron microscope (SEM) photograph of catalyst.
Fig. 2 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The X ray diffracting spectrum of catalyst.
Fig. 3 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The UV Diffuse Reflectance Spectroscopy figure of catalyst.
Fig. 4 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The forbidden bandwidth figure of catalyst.
Fig. 5 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The infrared spectrogram of catalyst.
Fig. 6 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The photoluminescence spectra figure of catalyst.
Fig. 7 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The comparison diagram of catalyst generation amount of carbon dioxide.
Fig. 8 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22Made from catalyst, comparative example 3 N-TiO2Cu-N-TiO made from catalyst and embodiment 12The performance comparison figure of catalyst Photocatalytic Degradation of Toluene.
Specific embodiment
Below by the drawings and specific embodiments, the present invention will be further described.
Comparative example 1
40mL dehydrated alcohol, 5mL butyl titanate and 10mL acetic acid are sequentially added into beaker, beaker is placed on magnetic agitation Magnetic agitation 30min on device obtains the first solution;Then 10mL deionized water is slowly dropped into the first solution, stirs 2h, obtains TiO2Colloidal sol after ageing for 24 hours, in 80 DEG C of at a temperature of drying 12h, after grinding, in 500 DEG C of Muffle kiln roasting 2h, obtains TiO2It urges Agent.
Photochemical properties test: the TiO made from comparative example 12The conversion ratio of catalyst Photocatalytic Degradation of Toluene, toluene is 10%。
Comparative example 2
40mL dehydrated alcohol, 0.071g copper nitrate, 5mL butyl titanate and 10mL glacial acetic acid are sequentially added into beaker, Magnetic agitation 30min on magnetic stirring apparatus, obtains solution A;Then 10mL deionized water is slowly dropped into solution A, stirs 2h, obtains Cu -TiO2Colloidal sol, ageing for 24 hours, in 80 DEG C of at a temperature of drying, after grinding, in 500 DEG C of Muffle kiln roasting 2h, obtain Cu-TiO2 Catalyst.
Photochemical properties test: the Cu-TiO made from comparative example 22Catalyst Photocatalytic Degradation of Toluene, the conversion of toluene Rate is 27.5%.
Comparative example 3
40mL dehydrated alcohol, 5mL butyl titanate and 10mL glacial acetic acid are sequentially added into beaker, beaker is placed on magnetic force and is stirred Magnetic agitation 30min on device is mixed, the second solution is obtained.0.353g urea is added in 10mL deionized water, is completely dissolved, obtains B solution, B solution is slowly dropped into the second solution, 2h is stirred, obtains N-TiO2Colloidal sol, after ageing for 24 hours, in 80 DEG C of at a temperature of drying 12h after grinding, in 500 DEG C of 2 h of Muffle kiln roasting, obtains N-TiO2Catalyst.
Photochemical properties test: the N-TiO made from comparative example 32Catalyst Photocatalytic Degradation of Toluene, the conversion ratio of toluene It is 28%.
Embodiment 1
40mL dehydrated alcohol, 0.071g copper nitrate, 5mL butyl titanate and 10mL glacial acetic acid are sequentially added into beaker, it will Beaker is placed on magnetic agitation 30min on magnetic stirring apparatus, obtains solution A;0.353g urea is added in 10mL deionized water, glass bar Stirring, is completely dissolved urea, obtains B solution;B solution is slowly dropped into solution A, 2h is stirred, obtains Cu-N-TiO2Colloidal sol, it is old After changing for 24 hours, in 80 DEG C of at a temperature of dry 12h, after grinding, in 500 DEG C of Muffle kiln roasting 2h, copper is made and nitrogen co-doped repairs Adorn titanium dioxide optical catalyst (Cu-N-TiO2Catalyst).
Photochemical properties test: the photochemical catalyst Photocatalytic Degradation of Toluene made from embodiment 1, the conversion ratio of toluene are 38%。
The characterization of copper made from embodiment 1 and nitrogen co-doped modified titanium dioxide photocatalyst:
1, SEM is tested
The scanning electron microscope (SEM) photograph of catalyst made from comparative example 1, comparative example 2, comparative example 3 and embodiment 1, as shown in Figure 1.Comparative example 1 TiO2The Cu-TiO of catalyst (Fig. 1 a), comparative example 22The N-TiO of catalyst (Fig. 1 b), comparative example 32Catalyst (Fig. 1 c) and The Cu-N-TiO of embodiment 12Catalyst (Fig. 1 d).It can be clearly seen that sample bolus is got together from figure, this is attributed to TiO2It the surface of nano particle can be very big, it is easy to reunite.Therefore, that observe in Electronic Speculum is TiO2Particle size Rather than crystallite dimension.As seen from Figure 1, pure TiO2Particle it is maximum, Cu-N-TiO2Particle is minimum.Suitable Cu's and N Incorporation can change TiO2Surface nature, make TiO2Surface can reduce, and then reduce TiO2Reunion between particle, shows The incorporation of Cu and N can inhibit the reunion of crystal grain well.
2, XRD diagram spectrum analysis
Fig. 2 is TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22N- made from catalyst, comparative example 3 TiO2Cu-N-TiO made from catalyst and embodiment 12The XRD of catalyst schemes.X-ray diffraction analysis (XRD) is for measuring crystalline substance Type structure, crystal form composition, crystallinity and crystallite dimension.It analyzes from Fig. 2 it is found that prepared sample shows stronger TiO2It is sharp Titanium ore characteristic diffraction peak (101) peak, Cu-TiO in figure2、N-TiO2And Cu-N-TiO2XRD spectrum it is identical, illustrate These three nano materials do not have any difference in terms of crystalline structure and particle size.Cu-TiO2、N-TiO2And Cu-N-TiO2With it is pure TiO2The sample crystallinity that compares becomes smaller, it is seen that the incorporation of Cu and N changes TiO2Size.
3, UV Diffuse Reflectance Spectroscopy figure and forbidden bandwidth atlas analysis
UV Diffuse Reflectance Spectroscopy is usually used in nano-TiO2The diffusing reflection of powder surface is analyzed, according to sample at different wavelengths anti- Rate is penetrated to detect the absorption spectrum under catalyst ultraviolet-visible light.TiO made from comparative example 12Made from catalyst, comparative example 2 Cu-TiO2N-TiO made from catalyst, comparative example 32Cu-N-TiO made from catalyst and embodiment 12The ultraviolet of catalyst is overflow Reflectance spectrum figure, as shown in Figure 3.Pure TiO2Catalyst is most weak in the absorption of visibility region, and Cu-TiO2Catalyst, N-TiO2 Catalyst and Cu-N-TiO2Red Shift Phenomena, Cu-N-TiO all has occurred in catalyst ABSORPTION EDGE2Catalyst UV Diffuse Reflectance Spectroscopy figure It shows most strong in visible region absorption.Light absorption threshold value is from pure TiO2400 nm extend to 550 nm, Cu-TiO2Catalysis Agent and Cu-N-TiO2Catalyst has stronger absorption in 400~550 nm of visible light region.The above phenomenon possible cause Be: suitable Cu doping can be in TiO2Valence band and conduction band between form intermediate level, make light induced electron and hole that transition occur The energy of Shi Suoxu reduces;And N doping can also cause TiO2Band gap narrows, to make TiO2Optical response range red shift to visible Light region.According to shock, you calculate band gap magnitude: (α hv)2=A(hv-Eg), wherein α, h, A and v correspond respectively to absorption coefficient, The characteristic constant and light frequency of Planck's constant, semiconductor material.Such as Fig. 4, TiO2Adulterate the semiconductor material after Cu and N Forbidden bandwidth narrows, and equally illustrates that material enhances the utilization rate of visible light.Semiconductor is calculated using the λ formula of Eg=1240/ Band gap magnitude TiO2、N-TiO2、Cu-TiO2And Cu-N-TiO2Forbidden bandwidth be respectively 3.11 eV, 3.03 eV, 2.51 EV and 2.28 eV.
4, infrared and photoluminescence spectra map analysis
TiO made from comparative example 12Cu-TiO made from catalyst, comparative example 22N-TiO made from catalyst, comparative example 32Catalysis Cu-N-TiO made from agent and embodiment 12The infrared spectrogram of catalyst, as shown in Figure 5.From fig. 5, it can be seen that being in wave number 3400 cm-1、1600 cm-1With 500~800 cm-1There is strong absworption peak respectively in place, in 3437 cm-1The absorption peak of left and right is answered TiO2The O-H stretching vibration of surface hydroxyl and absorption water, 1627 cm-1The absorption peak of left and right is TiO2The O-H of surface adsorption water Bending vibration, 500~800 cm-1The absorption peak of left and right is the characteristic peak of O-Ti-O.But from N-TiO2And Cu-N-TiO2's Do not occur the absorption peak of N-O in map, it may be possible to which, since doping is very little, signal is too weak not to be detected.
The service life of the photo-generated carrier of semiconductor catalyst is usually characterized with photoluminescence spectra, and fluorescence is usually utilized The power of intensity determines photo-generated carrier recombination rate height, and fluorescence intensity is weaker, and recombination rate is lower.TiO made from comparative example 12 Cu-TiO made from catalyst, comparative example 22N-TiO made from catalyst, comparative example 32Cu- made from catalyst and embodiment 1 N-TiO2The photoluminescence spectra figure of catalyst, as shown in Figure 6.It is observed that Cu-N-TiO2Fluorescence intensity than other Sample will be weak, show that the incorporation of Cu and N can effectively inhibit the compound of photo-generated carrier.
2The test of nano material photochemical properties:
Firstly, by the Cu-N-TiO of 0.1g2Nano material is put into reactor, is then injected into 20mL molal volume concentration and is The toluene aqueous solution of 0.05mol/L, is passed through the oxygen of a period of time, is sufficiently stirred half an hour on magnetic stirring apparatus and is adsorbed Processing finally opens light source and carries out illumination reaction.Every 30min that crosses detects gas concentration lwevel in reactor, wherein two The concentration of carbonoxide uses nitrogen enterprising as the gas-chromatography (GC-2080) of carrier gas with thermal conductivity detector (TCD) (TCD) Row detection.The gas in 0.6 mL reactor is taken with glass syringe, injects gas-chromatography.Toluene is calculated using following formula Conversion ratio:
Toluene conversion: Conversion %=(C0-C)/C0 × 100%
In formula, C0 is the initial concentration of toluene, and C is a certain concentration of toluene in reaction process.
By Fig. 7 it can be observed that the CO of the growth all samples with light application time2Yield be continuously increased, in illumination It is observed that Cu-N-TiO after two hours2CO2Yield reached 5800(ppm) left and right, be compared to pure TiO2 Improve nearly four times.This may be because when Cu mixes TiO2In, surface nature is improved, and intergranular reunion is reduced Phenomenon increases the specific surface area of particle, and Cu appropriate2+Capture trap can be formed and capture light induced electron, make light induced electron with Preferable separation is realized in hole, to improve Cu-N-TiO2Photocatalytic activity.Similarly, when N mixes TiO2In, N It may replace the O in Ti-O key, generate corresponding O vacancy, these O vacancies are conducive to TiO2The separation of middle light induced electron and hole, To be conducive to light-catalyzed reaction;And then improve Cu-N-TiO2Photocatalytic activity.
With pure TiO2For comparing, Cu-TiO2Catalyst, N-TiO2Catalyst and Cu-N-TiO2Catalyst is all shown Preferable catalytic performance.Light-catalyzed reaction 120 min, Cu-N-TiO2Catalyst has reached 38% to the conversion ratio of toluene, than phase Pure TiO under the conditions of2Catalytic activity improves nearly 4 times, as shown in Figure 8.
Embodiment 2
40mL dehydrated alcohol, 0.06g copper nitrate, 5mL butyl titanate and 15mL glacial acetic acid are sequentially added into beaker, will be burnt Cup is placed on magnetic agitation 50min on magnetic stirring apparatus, obtains solution A;0.24g urea is added in deionized water, and glass bar stirring makes Urea is completely dissolved, and obtains B solution;B solution is slowly dropped into solution A, 3h is stirred, obtains Cu-N-TiO2Colloidal sol, after being aged 22h, In 100 DEG C of at a temperature of drying 10h, after grinding, in 550 DEG C of Muffle kiln roasting 2h, copper and nitrogen co-doped modification dioxy is made Change titanium photochemical catalyst.
Embodiment 3
40mL dehydrated alcohol, 0.08g copper nitrate, 5mL butyl titanate and 12.5mL glacial acetic acid are sequentially added into beaker, it will Beaker is placed on magnetic agitation 40min on magnetic stirring apparatus, obtains solution A;0.32g urea is added in deionized water, glass bar stirring, It is completely dissolved urea, obtains B solution;B solution is slowly dropped into solution A, 2.5h is stirred, obtains Cu-N-TiO2Colloidal sol, ageing After 23h, in 90 DEG C of at a temperature of drying 11h, after grinding, in 525 DEG C of Muffle kiln roasting 3h, copper and nitrogen co-doped modification is made Titanium dioxide optical catalyst.
Embodiment 4
50mL dehydrated alcohol, 0.07g copper nitrate, 5mL butyl titanate and 10mL glacial acetic acid are sequentially added into beaker, will be burnt Cup is placed on magnetic agitation 35min on magnetic stirring apparatus, obtains solution A;0.35g urea is added in deionized water, and glass bar stirring makes Urea is completely dissolved, and obtains B solution;B solution is slowly dropped into solution A, 2h is stirred, obtains Cu-N-TiO2Colloidal sol, after being aged 23h, In 90 DEG C of at a temperature of drying 11h, after grinding, in 525 DEG C of Muffle kiln roasting 4h, copper and nitrogen co-doped modification titanium dioxide is made Titanium photochemical catalyst.
Embodiment 5
50mL dehydrated alcohol, 0.07g copper nitrate, 5mL butyl titanate and 15mL glacial acetic acid are sequentially added into beaker, will be burnt Cup is placed on magnetic agitation 45min on magnetic stirring apparatus, obtains solution A;0.42g urea is added in deionized water, and glass bar stirring makes Urea is completely dissolved, and obtains B solution;B solution is slowly dropped into solution A, 3h is stirred, obtains Cu-N-TiO2Colloidal sol, after ageing for 24 hours, In 100 DEG C of at a temperature of drying 10h, after grinding, in 500 DEG C of Muffle kiln roasting 3h, copper and nitrogen co-doped modification dioxy is made Change titanium photochemical catalyst.
Embodiment 6
50mL dehydrated alcohol, 0.065g copper nitrate, 5mL butyl titanate and 12.5mL glacial acetic acid are sequentially added into beaker, Beaker is placed on magnetic agitation 50min on magnetic stirring apparatus, obtains solution A;0.325g urea is added in deionized water, and glass bar stirs It mixes, is completely dissolved urea, obtain B solution;B solution is slowly dropped into solution A, 2.5h is stirred, obtains Cu-N-TiO2Colloidal sol, it is old After changing 22.5h, in 85 DEG C of at a temperature of drying 11.5h, after grinding, in 520 DEG C of Muffle kiln roasting 2.5h, copper is made and nitrogen is total Doping and modification titanium dioxide optical catalyst.
Embodiment 7
45mL dehydrated alcohol, 0.075g copper nitrate, 5mL butyl titanate and 10mL glacial acetic acid are sequentially added into beaker, it will Beaker is placed on magnetic agitation 50min on magnetic stirring apparatus, obtains solution A;0.3g urea is added in deionized water, glass bar stirring, It is completely dissolved urea, obtains B solution;B solution is slowly dropped into solution A, 3.5h is stirred, obtains Cu-N-TiO2Colloidal sol, ageing After 23.5h, in 95 DEG C of at a temperature of drying 10.5h, after grinding, in 530 DEG C of Muffle kiln roasting 3.5h, copper is made and nitrogen is co-doped with Miscellaneous modified titanium dioxide photocatalyst.
Embodiment 8
45mL dehydrated alcohol, 0.08g copper nitrate, 5mL butyl titanate and 15mL glacial acetic acid are sequentially added into beaker, will be burnt Cup is placed on magnetic agitation 50min on magnetic stirring apparatus, obtains solution A;0.48g urea is added in deionized water, and glass bar stirring makes Urea is completely dissolved, and obtains B solution;B solution is slowly dropped into solution A, 3.5h is stirred, obtains Cu-N-TiO2Colloidal sol, ageing After 23.5h, in 95 DEG C of at a temperature of drying 10.5h, after grinding, in 530 DEG C of Muffle kiln roasting 3.5h, copper is made and nitrogen is co-doped with Miscellaneous modified titanium dioxide photocatalyst.
Embodiment 9
45mL dehydrated alcohol, 0.072g copper nitrate, 5mL butyl titanate and 12.5mL glacial acetic acid are sequentially added into beaker, Beaker is placed on magnetic agitation 50min on magnetic stirring apparatus, obtains solution A;0.282g urea is added in deionized water, and glass bar stirs It mixes, is completely dissolved urea, obtain B solution;B solution is slowly dropped into solution A, 3.5h is stirred, obtains Cu-N-TiO2Colloidal sol, it is old After changing 23.5h, in 95 DEG C of at a temperature of drying 10.5h, after grinding, in 530 DEG C of Muffle kiln roasting 3.5h, copper is made and nitrogen is total Doping and modification titanium dioxide optical catalyst.

Claims (5)

1. the preparation method of a kind of copper and nitrogen co-doped modified titanium dioxide photocatalyst, which is characterized in that specifically press following step It is rapid to carry out:
1) 1 ︰, 8~10 ︰ 2~3 by volume takes butyl titanate, dehydrated alcohol and glacial acetic acid respectively, then presses four fourth of 5mL metatitanic acid The ratio of 0.06~0.08g copper nitrate is added in ester, takes copper nitrate;Urea, the quality of taken urea and taken copper nitrate are taken again Than for 4~6 ︰ 1;
Dehydrated alcohol, copper nitrate, butyl titanate and glacial acetic acid are mixed in order, stirs, obtains solution A;
Taken urea is dissolved completely in deionized water, is stirred evenly, B solution is obtained;
2) B solution is slowly dropped into solution A, stirs, obtains Cu-N-TiO2Colloidal sol;
3) by Cu-N-TiO2It is dry after colloidal sol ageing, it grinds, copper and nitrogen co-doped modified titanic oxide photocatalysis is made in roasting Agent.
2. the preparation method of copper as described in claim 1 and nitrogen co-doped modified titanium dioxide photocatalyst, which is characterized in that In the step 3), Cu-N-TiO2Colloidal sol is aged 22~24 h.
3. the preparation method of copper as described in claim 1 and nitrogen co-doped modified titanium dioxide photocatalyst, which is characterized in that In the step 3), Cu-N-TiO2After colloidal sol ageing, in 80 DEG C~100 DEG C of at a temperature of 10~12h.
4. the preparation method of copper as described in claim 1 and nitrogen co-doped modified titanium dioxide photocatalyst, which is characterized in that In the step 3), in 500 DEG C~550 DEG C of 2~4h of roasting temperature after grinding.
5. copper made from preparation method described in a kind of claim 1 and nitrogen co-doped modified titanium dioxide photocatalyst are in photocatalysis Application in degradation toluene.
CN201910369618.8A 2019-05-06 2019-05-06 The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the application for toluene of degrading Pending CN109999888A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910369618.8A CN109999888A (en) 2019-05-06 2019-05-06 The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the application for toluene of degrading

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910369618.8A CN109999888A (en) 2019-05-06 2019-05-06 The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the application for toluene of degrading

Publications (1)

Publication Number Publication Date
CN109999888A true CN109999888A (en) 2019-07-12

Family

ID=67175720

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910369618.8A Pending CN109999888A (en) 2019-05-06 2019-05-06 The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the application for toluene of degrading

Country Status (1)

Country Link
CN (1) CN109999888A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110227458A (en) * 2019-07-22 2019-09-13 四川轻化工大学 A kind of composite material of Copper-cladding Aluminum Bar mesoporous TiO 2 and its application
CN110449155A (en) * 2019-08-22 2019-11-15 南京林业大学 The preparation of copper ion modified nano-titanium dioxide and characterizing method
CN111632618A (en) * 2020-07-08 2020-09-08 青岛哈工程正和环保科技有限公司 Preparation method and application of supported double-doped modified titanium dioxide photocatalyst
CN111632619A (en) * 2020-06-17 2020-09-08 湖北民族大学 Copper-nitrogen co-doped titanium dioxide photocatalytic material, preparation method and application
CN111905753A (en) * 2020-08-10 2020-11-10 万华化学集团股份有限公司 Catalyst for catalyzing amine salt conversion, preparation method of catalyst and preparation method of DAM
CN113896236A (en) * 2021-09-13 2022-01-07 常州市妇幼保健院 Titanium dioxide synthesis method based on glutamine modification
CN114904522A (en) * 2021-02-09 2022-08-16 中国石油化工股份有限公司 Photocatalytic material and preparation method and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102274739A (en) * 2011-05-31 2011-12-14 中国科学院新疆理化技术研究所 Copper-nitrogen double-doped titanium dioxide photocatalytic material
CN104107706A (en) * 2014-07-15 2014-10-22 西安交通大学 Preparation method of nitrogen-iron codoped nanometer titania photocatalyst
CN104707641A (en) * 2015-02-15 2015-06-17 山东师范大学 Metal-nitrogen co-doped titanium dioxide hollow sphere catalyst and preparation method thereof
CN108993503A (en) * 2017-06-06 2018-12-14 天津城建大学 A method of copper/nitrogen is prepared based on xerogel-hydro-thermal method and is co-doped with nano TiO 2 powder
CN109574333A (en) * 2018-12-06 2019-04-05 东南大学 A kind of copper modification nitrogen-doped titanium dioxide material and its preparation method and application

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102274739A (en) * 2011-05-31 2011-12-14 中国科学院新疆理化技术研究所 Copper-nitrogen double-doped titanium dioxide photocatalytic material
CN104107706A (en) * 2014-07-15 2014-10-22 西安交通大学 Preparation method of nitrogen-iron codoped nanometer titania photocatalyst
CN104707641A (en) * 2015-02-15 2015-06-17 山东师范大学 Metal-nitrogen co-doped titanium dioxide hollow sphere catalyst and preparation method thereof
CN108993503A (en) * 2017-06-06 2018-12-14 天津城建大学 A method of copper/nitrogen is prepared based on xerogel-hydro-thermal method and is co-doped with nano TiO 2 powder
CN109574333A (en) * 2018-12-06 2019-04-05 东南大学 A kind of copper modification nitrogen-doped titanium dioxide material and its preparation method and application

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
CUIPING LIU ET AL.: "Comparison of the Photocatalytic Effi cience for Cu and N Co-Doped TiO2 by Sol-Gel and Xerogel-Hydrothermal Methods", 《MATERIALS TRANSACTIONS》 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110227458A (en) * 2019-07-22 2019-09-13 四川轻化工大学 A kind of composite material of Copper-cladding Aluminum Bar mesoporous TiO 2 and its application
CN110227458B (en) * 2019-07-22 2022-04-22 四川轻化工大学 Copper-doped mesoporous titanium dioxide composite material and application thereof
CN110449155A (en) * 2019-08-22 2019-11-15 南京林业大学 The preparation of copper ion modified nano-titanium dioxide and characterizing method
CN111632619A (en) * 2020-06-17 2020-09-08 湖北民族大学 Copper-nitrogen co-doped titanium dioxide photocatalytic material, preparation method and application
CN111632618A (en) * 2020-07-08 2020-09-08 青岛哈工程正和环保科技有限公司 Preparation method and application of supported double-doped modified titanium dioxide photocatalyst
CN111905753A (en) * 2020-08-10 2020-11-10 万华化学集团股份有限公司 Catalyst for catalyzing amine salt conversion, preparation method of catalyst and preparation method of DAM
CN111905753B (en) * 2020-08-10 2023-04-07 万华化学集团股份有限公司 Catalyst for catalyzing amine salt conversion, preparation method of catalyst and preparation method of DAM
CN114904522A (en) * 2021-02-09 2022-08-16 中国石油化工股份有限公司 Photocatalytic material and preparation method and application thereof
CN113896236A (en) * 2021-09-13 2022-01-07 常州市妇幼保健院 Titanium dioxide synthesis method based on glutamine modification

Similar Documents

Publication Publication Date Title
CN109999888A (en) The preparation of copper and nitrogen co-doped modified titanium dioxide photocatalyst and the application for toluene of degrading
Li et al. Efficient infrared light promoted degradation of volatile organic compounds over photo-thermal responsive Pt-rGO-TiO2 composites
Huang et al. Visible light Bi2S3/Bi2O3/Bi2O2CO3 photocatalyst for effective degradation of organic pollutions
Ni et al. New insights into how Pd nanoparticles influence the photocatalytic oxidation and reduction ability of gC 3 N 4 nanosheets
Dong et al. Synergistic integration of thermocatalysis and photocatalysis on black defective (BiO) 2 CO 3 microspheres
Jiao et al. Photocatalysts of 3D ordered macroporous TiO2-supported CeO2 nanolayers: design, preparation, and their catalytic performances for the reduction of CO2 with H2O under simulated solar irradiation
Gómez et al. Effect of sulfation on the photoactivity of TiO2 sol–gel derived catalysts
Patrocinio et al. Charge carrier dynamics and photocatalytic behavior of TiO 2 nanopowders submitted to hydrothermal or conventional heat treatment
Ni et al. A simple solution combustion route for the preparation of metal-doped TiO 2 nanoparticles and their photocatalytic degradation properties
EP2123605A1 (en) Production method of titanium dioxide (TIO2) photocatalyst and TIO2 photocatalyst produced by the same
Song et al. Oxygen defect-induced NO− intermediates promoting NO deep oxidation over Ce doped SnO2 under visible light
Sun et al. Dye degradation activity and stability of perovskite-type LaCoO3− x (x= 0∼ 0.075)
Mozia et al. Preparation of Fe-modified photocatalysts and their application for generation of useful hydrocarbons during photocatalytic decomposition of acetic acid
Kočí et al. Photocatalytic decomposition of methanol over La/TiO 2 materials
Navgire et al. β-Cyclodextrin supported MoO 3–CeO 2 nanocomposite material as an efficient heterogeneous catalyst for degradation of phenol
Gong et al. Constructing 1D/2D BiOI/ZnWO4 p‐n heterojunction photocatalyst with enhanced photocatalytic removal of NO
Liu et al. Liquid N2 quenching induced oxygen defects and surface distortion in TiO2 and the effect on the photocatalysis of methylene blue and acetone
CN108435226A (en) One kind preparing the flower-shaped TiO of N dopen Nanos using the lotus leaf that is carbonized as substrate2The method of catalysis material
CN108339544A (en) Photochemical catalyst/super-hydrophobic film composite material of fullerene carboxy derivatives modification
KR100966300B1 (en) Visible Rays Active Titanium Dioxide Codoped Carbon, Nitrogen, Boron, Fluorine and Manufacturing Method Thereof
Ren et al. Insights into the pivotal role of surface defects on anatase TiO2 nanosheets with exposed {001} facets for enhanced photocatalytic activity
Li et al. Photocatalytic oxidation of small molecule hydrocarbons over Pt/TiO 2 nanocatalysts
Espinosa et al. Synthesis and characterization of V2O5-Ga2O3 photocatalysts and their application on the photocatalytic reduction of CO2
Cerrato et al. Ternary systems based on ZnO/CeO2/Cu2O for the degradation of phenol and carbamazepine
Li et al. Fabrication of Rh-doped Bi2O3 with enhanced photocatalytic performance by sol-gel method

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
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20190712