CN106466604A - A kind of Cu2O/TiO2Composite photocatalyst material and preparation method thereof - Google Patents

A kind of Cu2O/TiO2Composite photocatalyst material and preparation method thereof Download PDF

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Publication number
CN106466604A
CN106466604A CN201611025221.XA CN201611025221A CN106466604A CN 106466604 A CN106466604 A CN 106466604A CN 201611025221 A CN201611025221 A CN 201611025221A CN 106466604 A CN106466604 A CN 106466604A
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tio
photocatalyst material
composite photocatalyst
preparation
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王艳芬
刘银
程详
张雷
徐初阳
李孟婷
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Anhui University of Science and Technology
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Anhui University of Science and Technology
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/72Copper
    • B01J35/39
    • B01J35/393
    • B01J35/51
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

The invention discloses a kind of Cu2O/TiO2Composite photocatalyst material, this material is to prepare classification TiO in hydro-thermal method2On the basis of hollow micro structure, surface ornament Cu2O nano-particle is thus obtain bigger serface and mushy classification Cu2O/TiO2Composite photocatalyst material.Cu of the present invention2O/TiO2The preparation process is simple of composite photocatalyst material, appearance structure is unique, not only the range expansion of photoresponse has been arrived visible region, and has shown excellent light degradation effect and good stable circulation performance in the process of organic dye waste water.

Description

A kind of Cu2O/TiO2Composite photocatalyst material and preparation method thereof
Technical field
The invention belongs to conductor photocatalysis material preparing technical field, particularly to a kind of Cu2O/TiO2Composite photocatalyst Material and preparation method thereof.
Background technology
In recent years, metal-oxide semiconductor (MOS) is turned in wastewater treatment and solar energy due to its high heliosensitivity and nontoxic essence The field of changing causes very big concern.As a kind of typical broad stopband n-type semiconductor, nano-TiO2Because of its photocatalytic activity High, cheap and stable performance is considered to solve environmental pollution and global energy supplies the study hotspot of problem, is at present A kind of conventional and the most promising photocatalyst.However, due to its wide energy gap (3.2ev), single TiO2Can only be in purple Response in outer optical range, the photo-generate electron-hole that it produces simultaneously, to being easy to be combined, leads to low sun light utilization efficiency and amount Sub- efficiency makes its practical application be very limited.
At present, a lot of methods are used to modify single TiO2Photocatalyst, such as:Composite semiconductor, dye sensitization, nonmetallic Or metallic element doping etc..Wherein, the coupling of narrow gap semiconductor is a kind of very effective method.Research shows compound half In conductor, narrow gap semiconductor by excited by visible light and can produce electron-hole pair.Due to different semiconductor conduction band and valence band The difference of position, makes light induced electron be gathered in a kind of conduction band of quasiconductor, and the valence band of another kind of quasiconductor is then transferred in hole, Electric charge carrier is sufficiently separated, and not only substantially increases photo-quantum efficiency, and by photoresponse range expansion to visible ray Region, thus improve light-catalysed efficiency.Cu2O, as a kind of narrow band gap (2.2eV) p-type semiconductor, has excellent light, electricity And catalysis characteristicses, if with broad stopband n-type semiconductor TiO2Compound, TiO will be improved most probably in terms of two above2Light urge Change activity, and show potential application prospect in terms of as photocatalyst for degrading organic pollution.Application No. 200910229191.8 invention one-dimensional Cu is prepared for using alternate electrodepostion process2O/TiO2Nucleocapsid structure array film;Application number Invention for 201010212628.X constructs Cu using impulse electrodeposition technology with reference to electroxidation method2O/TiO2Hetero-junctions is received Mitron array is although these methods all achieve the response in visible region for the product, but its product is one-dimensional array shape Looks, and operate route more complicated, it is related to apparatus expensive.Therefore, how to obtain pattern uniqueness, to have using easy syntheti c route The excellent Cu of visible light-responded and photocatalysis performance2O/TiO2Composite photo-catalyst is its key issue urgently to be resolved hurrily.
Content of the invention
It is an object of the invention to proposing novel C u that a kind of syntheti c route is simple and photocatalysis performance is excellent2O/TiO2Multiple Closing light catalysis material and preparation method thereof, the photocatalyst that it obtains not only can respond under visible light, and is applied To in organic dye waste water, degradation effect is notable.
The purpose of the present invention is achieved in the following ways.
A kind of Cu2O/TiO2Composite photocatalyst material it is characterised in that:This catalysis material is in classification TiO2The micro- knot of hollow Structure surface ornament Cu2O nano-particle obtains, wherein TiO2A diameter of 1-2 μm of hollow micro structure, Cu2The chi of O nano-particle Very little for 50-200nm.
A kind of Cu2O/TiO2The preparation method of composite photocatalyst material is it is characterised in that comprise the following steps:
(1) predecessor TiO2Preparation:Titanium potassium oxalate and hydrogen peroxide are separately added in deionized water, are adjusted using hydrochloric acid PH value, between 1~2, then reactant is added in hydrothermal reaction kettle, reacts 12h at 150 DEG C, product is cooled down, is centrifuged, Wash, be dried.
(2)Cu2O/TiO2The preparation of composite photocatalyst material:By the TiO in step (1)2All it is distributed to 10mL deionization In water, under conditions of magnetic agitation, make unit for uniform suspension, be then respectively adding acetic acid copper liquor, NaOH aqueous solution and lemon Lemon aqueous acid, under 50 DEG C of water bath condition, then product is centrifuged, washs, is vacuum dried by continuing magnetic force stirring 30min.
In step (1), the quality of described titanium potassium oxalate is 1.56g;The concentration of described hydrogen peroxide is 30%, and volume is 2mL;The volume of described deionized water is 30-40mL:The concentration of described hydrochloric acid is 37%;Described hydrothermal reaction kettle is polytetrafluoroethyl-ne The stainless steel cauldron of alkene inner bag, volume is 50mL;The temperature of described drying is 80-100 DEG C.
In step (2), the concentration of described acetic acid copper liquor is 0.062g/mL, and volume is 16mL;Described NaOH is water-soluble The concentration of liquid is 0.28g/mL, and volume is 16mL;The concentration of described aqueous citric acid solution is 0.16g/mL, and volume is 10mL;Institute State dry temperature and be 60-80 DEG C.
Compared with existing technology at present, Cu is prepared using the inventive method2O/TiO2Composite photocatalyst material has following Advantage:
1st, the inventive method adopts two step liquid phase method synthesis Cu2O/TiO2Composite photocatalyst material, is sunk with the electricity of current report Area method is compared, and preparation process is simple, is not related to the equipment of complicated loaded down with trivial details operation and costliness;Raw material is cheap and easily-available simultaneously, cost Relatively low, and products collection efficiency is higher, suitable industrialized production.
2nd, the Cu of the inventive method preparation2O/TiO2Composite photocatalyst material, is by classification TiO2Hollow micro structure and growth A large amount of Cu on its surface2O nano-particle assembles, and its unique structure makes it have big specific surface area and many holes Gap, has the dispersion using hydroxyl radical free radical in organic molecule in quickening waste water and photochemical reaction and transport, thus significantly improving Its photocatalysis performance.
3rd, the Cu of the inventive method preparation2O/TiO2Composite photocatalyst material, with single-phase TiO2Compare, the model of photoresponse Enclose and extend to visible region from UV light region, improve the utilization rate of sunlight;Simultaneously because Cu2The conduction band of O and valency Band position is above TiO2, narrow gap semiconductor Cu2O excites the electronics of generation to be easy to transfer to TiO under visible light2Lead On band, and Cu is then stayed in hole2So that photo-generated carrier obtains very big separation in the valence band of O, effectively inhibit answering of the two Close, and then significantly improve the photocatalysis performance of its complex.
4th, adopt the Cu of the inventive method preparation2O/TiO2Composite photocatalyst material, not only in the process of organic dye waste water In there is good light degradation effect, and show preferable stable circulation performance, beneficial to being recycled for multiple times.
Brief description
Fig. 1 is X-ray diffraction (XRD) spectrogram of three kinds of different products:(a)Cu2O/TiO2, (b) TiO2, (c) Cu2O;
Fig. 2 is scanning electron microscope (SEM) picture of three kinds of different products:(a,b)Cu2O/TiO2, (c) TiO2, (d) Cu2O;
Fig. 3 (a-c) is product Cu of the present invention2O/TiO2Transmission electron microscope (TEM) photo of composite photocatalyst material, (d) is figure The energy dispersive spectrum (EDS) of roundel in 3a;
Fig. 4 is single TiO2、Cu2O and product Cu of the present invention2O/TiO2UV-visible absorption spectrum (a) and corresponding The energy gap (b) of the three kinds of materials calculating;
Fig. 5 (a) is product Cu of the present invention2O/TiO2Purple as photocatalyst degradation of methylene blue solution under visible light Outward-visible absorbance collection of illustrative plates, (b) is the disposal efficiency of the different products of blank experiment and three kinds degradation of methylene blue under visible light Comparison diagram.
Fig. 6 is product Cu of the present invention2O/TiO2The recycling performance test chart of composite photocatalyst material.
Specific implementation steps
Further describe the present invention below by embodiment.It will be appreciated, however, that described herein be embodied as Example, only in order to explain the present invention, not limits the scope of the present invention.
Embodiment 1:
Weigh 1.56g K2TiO(C2O4)2It is dissolved in 30mL deionized water, be slowly added 2mL H2O2(30%) and constantly Stirring makes solution fully react, and it is 2 that the dilute HCl of Deca (37%) adjusts PH;Then reaction solution is poured into 50mL rustless steel hydro-thermal In reactor, react 12h at 150 DEG C.After question response terminates, product natural cooling carries out centrifugal treating using centrifuge, use Deionized water and dehydrated alcohol repeatedly wash, and 12h is dried at 80 DEG C, that is, obtain single TiO2Predecessor.
TiO by above-mentioned acquisition2It is dispersed in 10mL deionized water, make even suspension under conditions of magnetic agitation Liquid, is then respectively adding 16mL acetic acid copper liquor (0.062g/mL), 16mLNaOH aqueous solution (0.28g/mL) and 10mL anti-bad Hematic acid aqueous solution (0.16g/mL), under 50 DEG C of water bath condition, then product is centrifuged, washs by continuing magnetic force stirring 30min, 60 DEG C of dryings under vacuum conditions, that is, obtain product Cu2O/TiO2Composite photocatalyst material.In order to as a comparison, without TiO2Under conditions of predecessor, single Cu is prepared using similar synthetic route2O sample.
The product of acquisition is carried out performance test.Carry out the crystal structure of product using X-ray powder diffraction instrument (XRD) Test;Observe the microscopic appearance of product using scanning electron microscope (SEM) and transmission electron microscope (TEM);Using ultraviolet- Visible spectrophotometer carries out optical property test to product;Come using degradating organic dye methylene blue solution under radiation of visible light Evaluate the photocatalysis performance of product;Using the degradation rate to methylene blue solution for radiation of visible light 3 products of lower recycling To evaluate the stability of product.Wherein, the specific experiment step of degradating organic dye methylene blue solution is as follows:Take 100mL, 5×10-5The methylene blue solution of mol/L, as target degradation product, weighs 50mg sample and is added in above-mentioned solution, hold at dark place Continuous stirring 60min is balanced in the adsorption-desorption of catalyst surface with reaching methylene blue, then with 420nm filter plate 300W xenon lamp irradiates.Take a suspension (3mL) at illumination 30min interval, after centrifugation, use ultraviolet-uisible spectrophotometer The absorbance of the methylene blue solution after measurement different time photocatalysis.Its fall is assessed by the resolution ratio calculating methylene blue Solution effect, computing formula is as follows:
Resolution ratio (%)=(C0-C)/C0× 100, C0With the methylene blue solution absorbance before and after C respectively illumination.
In the XRD spectra of the different products of Fig. 1 be given three kinds, all diffraction maximums in Fig. 1 b and TiO2JCPDS card (21-1276) consistent, the diffraction maximum in Fig. 1 c and Cu2The JCPDS card (05-0667) of O consistent it was demonstrated that produce Thing is respectively cubic Rutile Type TiO2With Emission in Cubic Cu2O.The each diffraction peak intensity of in figure is higher, does not have other impurity peaks to occur, Illustrate that the purity of product is very high, and there is good crystallinity.Diffraction maximum in Fig. 1 a then can be classified as Rutile Type TiO2With Emission in Cubic Cu2O is it was demonstrated that this product is by Cu2O and TiO2The biphase complex of composition.
Fig. 2 gives the SEM picture of three kinds of different products.By with single-phase TiO2And Cu2O pattern contrast it can be seen that Cu2O/TiO2Product is by classification hollow micro structure TiO of about 1-2 μm of diameter2It is 50- with the size being grown in its surfaces externally and internally The Cu of 200nm2O nano-particle assembles so as to present big roughness and many pore structures.
Fig. 3 is Cu2O/TiO2The TEM picture of composite photocatalyst material and EDS picture.Picture further demonstrate that XRD and Phenomenon what is observed in SEM:This product is by middle space stage TiO2With a large amount of Cu2O nano-particle assembles.
Fig. 4 is the UV-visible absorption spectrum of three kinds of different products and corresponding energy gap.Can from figure Go out, product Cu of the present invention2O/TiO2The energy gap (2.69eV) of composite photocatalyst material is different from single-phase TiO2(2.87eV) With single-phase Cu2O (2.2eV), and all have the absorption of light in ultraviolet light and visible region, photoresponse scope substantially extends.
Fig. 5 (a) shows under visible light illumination, product Cu of the present invention2O/TiO2Make methylene blue molten as photocatalyst Characteristic absorption peak intensity at 665nm for the liquid constantly reduces with the prolongation of light application time, vanishes from sight, say after irradiating 120min Methylene blue in bright now solution is completely degraded.In Fig. 5 (b), after radiation of visible light 120min, single-phase TiO2With Cu2The degradation rate respectively 26% and 32% to methylene blue for the O, and Cu2O/TiO2The degraded to methylene blue for the composite photo-catalyst Rate nearly reaches 100%.This result shows, with single photocatalyst (TiO2、Cu2O) compare, Cu2O/TiO2Composite photocatalyst Agent has the excellent photocatalysis performance being remarkably reinforced.
Recycle performance test chart 6 and show in the degraded of methylene blue solution under visible light, this product Cu2O/ TiO2After composite photo-catalyst recycles three times, its photocatalytic degradation efficiency has almost no change, and implys that product has good Good stability and recycling performance.

Claims (4)

1. a kind of Cu2O/TiO2Composite photocatalyst material it is characterised in that:This catalysis material is in classification TiO2Hollow micro structure Surface ornament Cu2O nano-particle obtains, wherein TiO2A diameter of 1-2 μm of hollow micro structure, Cu2The size of O nano-particle For 50-200nm.
2. a kind of preparation method of composite photocatalyst material described in claim 1 is it is characterised in that comprise the following steps:
(1) predecessor TiO2Preparation:Titanium potassium oxalate and hydrogen peroxide are separately added in deionized water, pH value is adjusted using hydrochloric acid To between 1~2, then reactant is added in hydrothermal reaction kettle, reacts 12h at 150 DEG C, product is cooled down, be centrifuged, wash Wash, be dried.
(2)Cu2O/TiO2The preparation of composite photocatalyst material:By the TiO in step (1)2All it is distributed to 10mL deionized water In, make unit for uniform suspension under conditions of magnetic agitation, be then respectively adding acetic acid copper liquor, NaOH aqueous solution and Fructus Citri Limoniae Aqueous acid, under 50 DEG C of water bath condition, then product is centrifuged, washs, is vacuum dried by continuing magnetic force stirring 30min.
3. composite photocatalyst material according to claim 2 preparation method it is characterised in that:In step (1), described The quality of titanium potassium oxalate is 1.56g;The concentration of described hydrogen peroxide is 30%, and volume is 2mL;The volume of described deionized water is 30-40mL:The concentration of described hydrochloric acid is 37%;Described hydrothermal reaction kettle is the stainless steel cauldron of polytetrafluoroethylliner liner, body Amass as 50mL;The temperature of described drying is 80-100 DEG C.
4. composite photocatalyst material according to claim 2 preparation method it is characterised in that:In step (2), described The concentration of acetic acid copper liquor is 0.062g/mL, and volume is 16mL;The concentration of described NaOH aqueous solution is 0.28g/mL, volume For 16mL;The concentration of described aqueous citric acid solution is 0.16g/mL, and volume is 10mL;The temperature of described drying is 60-80 DEG C.
CN201611025221.XA 2016-11-22 2016-11-22 A kind of Cu2O/TiO2Composite photocatalyst material and preparation method thereof Pending CN106466604A (en)

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CN106944052A (en) * 2017-03-27 2017-07-14 曲靖师范学院 Cu2+1O/Cu2Cl(OH)3/TiO2Ternary complex and preparation method thereof
CN107233922A (en) * 2017-06-19 2017-10-10 天津城建大学 A kind of stone-like C2O7Ti2·3H2O photochemical catalysts and preparation method thereof
CN108169308A (en) * 2017-12-28 2018-06-15 中南大学 A kind of preparation method and applications of clay modified electrode
CN109865514A (en) * 2019-03-26 2019-06-11 武汉工程大学 A kind of preparation method of copper/titanic oxide composite photochemical catalyst material
CN109876809A (en) * 2019-04-01 2019-06-14 中国科学院过程工程研究所 A kind of hollow more Shell Materials of metal composite oxide and its preparation method and application
CN110882699A (en) * 2019-12-06 2020-03-17 四川源景绿能科技有限公司 Photocatalyst based on triple heterojunction structure and preparation method thereof
CN112823881A (en) * 2019-11-21 2021-05-21 中国科学院兰州化学物理研究所 Sea urchin-like titanium dioxide/cuprous oxide composite material, and preparation method and application thereof
CN113181912A (en) * 2021-03-26 2021-07-30 南京信息工程大学 Cu2O-TiO2Composite photocatalyst and preparation method and application thereof
CN113368854A (en) * 2021-06-10 2021-09-10 西南林业大学 Nano TiO (titanium dioxide)2/Cu2Preparation method of O porous composite material
CN116351417A (en) * 2023-03-17 2023-06-30 陕西净豹新材料有限公司 Preparation method of composite nano catalytic material for removing nitrogen oxides in atmospheric environment

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CN106944052B (en) * 2017-03-27 2020-01-31 曲靖师范学院 Cu2+1O/Cu2Cl(OH)3/TiO2Ternary complex and preparation method thereof
CN106944052A (en) * 2017-03-27 2017-07-14 曲靖师范学院 Cu2+1O/Cu2Cl(OH)3/TiO2Ternary complex and preparation method thereof
CN106824233A (en) * 2017-03-27 2017-06-13 曲靖师范学院 The method of photocatalysis antibacterial or degradation of organic substances
CN106824233B (en) * 2017-03-27 2019-07-19 曲靖师范学院 The method of photocatalysis antibacterial or degradation of organic substances
CN107233922A (en) * 2017-06-19 2017-10-10 天津城建大学 A kind of stone-like C2O7Ti2·3H2O photochemical catalysts and preparation method thereof
CN107233922B (en) * 2017-06-19 2019-08-30 天津城建大学 A kind of stone-like C2O7Ti2·3H2O photochemical catalyst and preparation method thereof
CN108169308A (en) * 2017-12-28 2018-06-15 中南大学 A kind of preparation method and applications of clay modified electrode
CN108169308B (en) * 2017-12-28 2020-11-06 中南大学 Preparation method and application of clay modified electrode
CN109865514A (en) * 2019-03-26 2019-06-11 武汉工程大学 A kind of preparation method of copper/titanic oxide composite photochemical catalyst material
CN109876809B (en) * 2019-04-01 2020-10-09 中国科学院过程工程研究所 Composite metal oxide hollow multi-shell material and preparation method and application thereof
CN109876809A (en) * 2019-04-01 2019-06-14 中国科学院过程工程研究所 A kind of hollow more Shell Materials of metal composite oxide and its preparation method and application
CN112823881A (en) * 2019-11-21 2021-05-21 中国科学院兰州化学物理研究所 Sea urchin-like titanium dioxide/cuprous oxide composite material, and preparation method and application thereof
CN112823881B (en) * 2019-11-21 2022-04-08 中国科学院兰州化学物理研究所 Sea urchin-like titanium dioxide/cuprous oxide composite material, and preparation method and application thereof
CN110882699A (en) * 2019-12-06 2020-03-17 四川源景绿能科技有限公司 Photocatalyst based on triple heterojunction structure and preparation method thereof
CN113181912A (en) * 2021-03-26 2021-07-30 南京信息工程大学 Cu2O-TiO2Composite photocatalyst and preparation method and application thereof
CN113368854A (en) * 2021-06-10 2021-09-10 西南林业大学 Nano TiO (titanium dioxide)2/Cu2Preparation method of O porous composite material
CN116351417A (en) * 2023-03-17 2023-06-30 陕西净豹新材料有限公司 Preparation method of composite nano catalytic material for removing nitrogen oxides in atmospheric environment

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