CN107930633B - Preparation method and application of SrTiO3/Cu2O heterojunction composite nano material - Google Patents

Preparation method and application of SrTiO3/Cu2O heterojunction composite nano material Download PDF

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CN107930633B
CN107930633B CN201711180113.4A CN201711180113A CN107930633B CN 107930633 B CN107930633 B CN 107930633B CN 201711180113 A CN201711180113 A CN 201711180113A CN 107930633 B CN107930633 B CN 107930633B
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stirring
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CN107930633A (en
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胡可军
夏咏梅
卢雅琳
王洪金
孙顺平
李小平
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Jiangsu University of 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
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • 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
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/78Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with alkali- or alkaline earth metals
    • B01J35/39
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

Abstract

Novel SrTiO3/Cu2The preparation method of the O-junction composite nano material comprises the following steps: dissolving (tetra) isopropyl titanate and strontium chloride hexahydrate in acid respectively, mixing, adjusting the pH value to 3-4, heating to 90 ℃, and preserving heat for 3 hours; then heating to 400-500 ℃, and preserving heat for 4-6 hours; obtaining SrTiO3A catalyst; stirring and dissolving copper acetate dihydrate in glycol monomethyl ether at 35 ℃, stirring, performing ultrasonic treatment for 60 minutes, and then adding SrTiO3Stirring a catalyst, adding a sodium hydroxide solution, adjusting the pH value to 10-14, and stirring for 10 minutes at 50 ℃; adding sufficient glucose solution, and reacting for 1-1.5 hours; cooling to room temperature, and performing centrifugal separation to obtain a precipitate solid. SrTiO of the invention3/Cu2SrTiO in O heterogeneous composite catalyst3And Cu2The heterojunction is formed by O, the application of the electron and the hole is facilitated, the heterojunction catalyst degrades organic dye wastewater under visible light, and particularly the photocatalytic degradation efficiency of methylene blue organic solution reaches 92%.

Description

Preparation method and application of SrTiO3/Cu2O heterojunction composite nano material
Technical Field
The invention belongs to the field of photocatalytic materials, and particularly relates to a preparation method and application of a SrTiO3/Cu2O heterojunction composite nano material.
Background
In recent years, the dye industry in China is rapidly developed, according to incomplete statistics, about 90-100 million tons of various dye sewage are discharged every day in China, and dye wastewater becomes one of the environmental important pollution sources. The dye industry has various varieties and complex processes, and the waste water contains a large amount of organic matters, has the characteristics of high CODCr, dark color, strong acid-base property and the like, and is always a difficult problem in waste water treatment. Therefore, the development of novel water treatment materials and novel processes, and the control of toxic organic pollutants become one of the key problems to be solved urgently in the environmental field. Extensive and intensive research for decades shows that organic pollutants can be completely converted and decomposed into inorganic small molecular substances such as CO2, H2O and the like by utilizing the photocatalysis of semiconductors such as ZnO, TiO2 and the like, and the method has the advantages of mild reaction conditions, low energy consumption, safety, no toxicity and simple and convenient operation, and is regarded as an ideal high-efficiency and low-consumption green environment treatment technology and is paid attention by environmental experts.
SrTiO3 is a semiconductor material developed on the basis of TiO2, and has wide application in the fields of photolysis of water to produce hydrogen and mineralization of organic substances (Yan Jian Hui, j.a. com., 472(2009) 429-433). Although SrTiO3 has a forbidden band width of 3.4eV and mainly absorbs ultraviolet light, it is significant to study a catalytic material having high photocatalytic activity under ultraviolet-visible light in order to effectively utilize sunlight, since ultraviolet light (below 420 nm) is less than 5% and visible light having a wavelength of 420 to 750nm accounts for 43% in the solar spectrum, and it is a necessary trend for photocatalytic development to be further put into practical use to find an inexpensive and high-performance ultraviolet-visible photocatalytic material. The previous reports mostly aim at the research of SrTiO3 monomer, and the Cr doping method is utilized by Chang et al (Chia-Hao Chang, Materials Letters, 60 (1): 129-132), so that SrTiO3 has visible light response, the degradation capability of methylene blue is greatly improved, and a good idea is provided for expanding the light absorption range of the SrTiO 3. Takeshi et al (Takeshi Toshima, Crystal.growth Des., 2008, 8 (7): 2066-2069) prepare perovskite type with multi-edge three-dimensional structure by a special crystal growth control method
SrTiO3 has new characteristics in light absorption characteristics and crystal structure. Yuan et al (RS Yuan, ACCcatal., 2011, 1 (3): 200-206) studied TiO2 with chlorine modified surface and some titanium-based composites, and proved that the photocatalytic degradation is remarkably improved. The document reports that cuprous oxide (Cu2O) belongs to a P-type semiconductor, the forbidden band width is about 2.2ev, the absorption wavelength is 563.nm, visible light can be absorbed, sunlight can be converted into electric energy or chemical energy, and therefore the cuprous oxide can generate a photocatalytic reaction under the irradiation of sunlight and is a photocatalyst with extremely high potential. The SrTiO3/Cu2 heterojunction composite material is constructed by taking a nano heterojunction theory as an idea and combining the energy band matching characteristics of SrTiO3 and Cu 2O.
The Chinese patent with publication number CN102698787A discloses a method for preparing a photocatalyst with high activity and large specific surface area by a novel solid phase method, which relates to a method for preparing a CN/SrTiO3 composite photocatalyst, and the preparation method of the catalyst is as follows: dissolving butyl titanate, Sr (NO3)3 and citric acid in ethylene glycol, and mixing to obtain a solution; carrying out ultrasonic treatment and microwave treatment on the solution to obtain sol, dehydrating the sol to form gel, firing the gel into powder, grinding the powder, and roasting at the temperature of 600-1000 ℃ for 8-15 h to obtain a SrTiO3 precursor; mixing and grinding the SrTiO3 precursor and urea, roasting to obtain a crude product, washing the crude product, and drying to obtain the composite photocatalyst. The product obtained by the method has good dispersibility, does not need acidic conditions when in use, can completely degrade rhodamine B within 50min, and is used for decomposing water to produce hydrogen, photodegrading organic matters and the like.
The invention patent with the publication number of CN103949200A discloses a preparation method of a NiFe2O4/Cu2O magnetic compound, and the photocatalytic degradation efficiency of the obtained compound on nitrophenol solution reaches 61.18%. However, in the existing documents, the preparation process is complex, takes a long time, and the prepared catalyst has the defects of large particles, small specific surface area, low photocatalytic degradation efficiency and the like.
Chinese patent with the patent number CN103464133A discloses a preparation method and application of a novel SrTiO3/TiO2 composite photocatalytic material. The catalyst is prepared by synthesizing SrTiO3 by adopting a coprecipitation method, doping the SrTiO3 into TiO2 by utilizing a sol-gel method, and finally performing surface chlorination modification by utilizing an impregnation method to obtain the novel composite photocatalyst. The preparation method comprises the following specific operation steps: adding SrTiO3 powder into 150ml of titanium glue according to the mass ratio of 18%, violently stirring for 24 hours, and drying by microwave; sintering the mixture for 3 to 5 hours in a muffle furnace at the temperature of between 400 and 500 ℃ to obtain the SrTiO3/TiO2 composite photocatalytic material; soaking 1g of the compound in 2ml of concentrated hydrochloric acid, sealing and standing in dark for 24h, then placing in a fume hood with an opening until the hydrochloric acid is completely volatilized, and finally drying at 50-60 ℃. The composite catalyst has the characteristics of high catalytic activity, wide applicability and good stability. Under the ultraviolet condition, the gas phase photocatalysis performance of the novel material is greatly improved compared with that of pure TiO2, and the novel material has great potential in the aspects of atmospheric pollution treatment, water treatment and the like
The Chinese patent with the publication number of CN10106964338A discloses a preparation method and application of a novel WO3/SrTiO3 composite photocatalytic material. The Chinese patent with the publication number of CN105817217A discloses a SrTiO 3/graphene composite catalyst, and a preparation method and application thereof. Researches show that the graphene and the photocatalytic material can be compounded to be used as an electron transfer medium to improve the migration rate of photo-generated electrons in a semiconductor, reduce the recombination rate of current carriers and improve the photocatalytic quantum efficiency of the semiconductor material.
In recent years, researchers have conducted a great deal of research work around SrTiO3, but related patents and technologies have low catalytic efficiency, and no SrTiO3/Cu2O heterogeneous composite catalyst has been reported so far.
Disclosure of Invention
In order to solve the defect that the catalytic efficiency of the composite catalyst of SrTiO3 is low and still low in the prior art, the invention provides a SrTiO3/Cu2O heterogeneous composite catalyst.
A preparation method of SrTiO3/Cu2O heterojunction composite nano-materials comprises the following steps:
1) respectively dissolving (tetra) isopropyl titanate and strontium chloride hexahydrate in acetic acid and citric acid, and stirring for 10-20 minutes;
2) mixing a (tetra) isopropyl titanate solution and a strontium chloride hexahydrate solution, uniformly stirring, adjusting the pH value to 3-4, heating to 90 ℃, preserving heat for 3 hours, and transferring to a reaction kettle;
3) heating the reaction kettle to 400-500 ℃, and preserving heat for 4-6 hours; separating, washing and drying the obtained powder solid to obtain SrTiO3 catalyst;
4) stirring and dissolving copper acetate dihydrate into glycol monomethyl ether at 35 ℃, stirring for 10-20 minutes, and carrying out ultrasonic treatment for 60 minutes to obtain a copper acetate solution;
5) adding the SrTiO3 catalyst obtained in the step 3) into the solution 4), stirring for 10-20 minutes, adding a sodium hydroxide solution, adjusting the pH value to 10-14, and stirring for 10 minutes at 50 ℃;
6) adding sufficient glucose solution, and reacting for 1-1.5 hours; cooling to room temperature, and performing centrifugal separation to obtain a precipitate solid;
7) and washing the precipitated solid obtained in the step 6) with clear water, drying and drying to obtain the SrTiO3/Cu2O heterojunction composite nano material.
Furthermore, the molar ratio of the added SrTiO3 catalyst in the step (5) to the copper acetate in the solution is 3: 2-1: 4. Preferably, the molar ratio of the SrTiO3 catalyst to the copper acetate in the solution is 2-1.
Further, the molar ratio of the added glucose in the step (6) to the copper acetate in the solution is 1:1-1: 1.5.
Further, the molar ratio of the titanium atoms to the strontium atoms in the step (1) is 1:1.
Further, the concentration of the copper acetate dihydrate solution in the step (4) is 0.1 mol per liter.
Further, the concentration of acetic acid in the step (1) is 2 mol per liter, and the concentration of citric acid is 4mol per liter.
Has the advantages that: in the SrTiO3/Cu2O heterogeneous composite catalyst, SrTiO3 and Cu2O form a heterojunction, so that the application of electrons and holes is facilitated, the heterojunction catalyst degrades organic dye wastewater under visible light, and particularly the photocatalytic degradation efficiency of a methylene blue organic solution reaches 92%.
Drawings
FIG. 1 is a spectrum of XRD of SrTiO3/Cu2O
FIG. 2 is an SEM picture of SrTiO3/Cu2O composite nanoparticles
FIG. 3 is a Uv-Vis spectrum of SrTiO3/Cu 2O.
FIG. 4 shows the degradation effect of SrTiO3/Cu2O heterojunction composite nano-material on methylene blue solution.
Detailed Description
Examples
A preparation method of SrTiO3/Cu2O heterojunction composite nano-materials comprises the following steps:
1) 2.8422g of (tetra) isopropyl titanate is weighed and dissolved in 24mL of acetic acid solution, the solution is continuously stirred for 10 to 20 minutes, and 20mL of deionized water is added at the same time;
weighing 2.6662g of strontium chloride hexahydrate, respectively dissolving in 4mol/l of citric acid, and stirring for 10-20 minutes;
2) mixing a (tetra) isopropyl titanate solution and a strontium chloride hexahydrate solution, uniformly stirring, adjusting the pH value to 3.5, heating to 90 ℃, preserving heat for 3 hours, and then transferring to a reaction kettle;
3) heating the reaction kettle to 400-500 ℃, and preserving heat for 5 hours; separating, washing and drying the obtained powder solid to obtain SrTiO3 catalyst;
4) 1.9965g of copper acetate dihydrate is stirred and dissolved in 100mL of glycol methyl ether at 35 ℃, stirred for 15 minutes and ultrasonically treated for 60 minutes to obtain 0.1 mol of copper acetate solution per liter;
5) adding 0.9173g of SrTiO3 catalyst obtained in the step 3) into the solution 4), stirring the mixture for 15 minutes, adding 24mL of 0.04g/mL sodium hydroxide solution, adjusting the pH value to 10, and stirring the mixture for 10 minutes at 50 ℃;
6) adding 24mL of 0.05g/mL glucose solution, and reacting for 1 hour; cooling to room temperature, and performing centrifugal separation to obtain a precipitate solid;
7) and washing the precipitated solid obtained in the step 6) with clear water, and drying in a vacuum oven at the temperature of 80 ℃ for 8 hours to obtain the SrTiO3/Cu2O heterojunction composite nano-material.
The spectrum analysis of XRD of SrTiO3/Cu2O prepared by the method is shown in figure 1. SEM analysis and detection of the SrTiO3/Cu2O prepared by the embodiment shows that the composite nano-particles have the size of about 500-1.5 μm as shown in figure 2. The results of UV-VIS spectroscopy analysis of SrTiO3/Cu2O prepared in this example are shown in FIG. 3.
0.5g of SrTiO3/Cu2O prepared in example was added to 100mL of 20mg/L methylene blue solution, and the solution was placed under a 500W UV-visible lamp to perform a photocatalytic reaction, wherein the distance from the light source to the reaction solution surface was 20 cm. The best degradation rate of 1SrTiO3/1Cu2O after 60 minutes of photocatalysis reaches 92%, as shown in FIG. 4, FIG. 4 shows that the better catalytic effect can be achieved when the molar ratio of SrTiO3 or Cu2O in the SrTiO3/Cu2O heterojunction composite nano-material is greatly influenced than the catalytic performance of the composite nano-material, but the SrTiO3 or Cu2O is not mixed in any ratio, wherein the catalytic performance of the SrTiO3/Cu2O heterojunction composite nano-material is the best when the molar ratio of SrTiO3 to Cu2O is 1:1.

Claims (8)

1. SrTiO3/Cu2The preparation method of the O heterojunction composite nano material is characterized by comprising the following steps of:
1) respectively dissolving (tetra) isopropyl titanate and strontium chloride hexahydrate in acetic acid and citric acid, and stirring for 10-20 minutes;
2) mixing a (tetra) isopropyl titanate solution and a strontium chloride hexahydrate solution, uniformly stirring, adjusting the pH value to 3-4, heating to 90 ℃, preserving heat for 3 hours, and transferring to a reaction kettle;
3) heating the reaction kettle to 400-500 ℃, and preserving heat for 4-6 hours; separating, washing and drying the obtained powder solid to obtain SrTiO3A catalyst;
4) stirring and dissolving copper acetate dihydrate into glycol monomethyl ether at 35 ℃, stirring for 10-20 minutes, and carrying out ultrasonic treatment for 60 minutes to obtain a copper acetate solution;
5) adding 3) the SrTiO to 4)3Stirring the catalyst for 10-20 minutes, adding a sodium hydroxide solution, adjusting the pH value to 10-14, and stirring for 10 minutes at 50 ℃;
6) adding sufficient glucose solution, and reacting for 1-1.5 hours; cooling to room temperature, and performing centrifugal separation to obtain a precipitate solid;
7) washing the precipitated solid obtained in the step 6) with clear water, drying and drying to obtain SrTiO3/Cu2And O heterojunction composite nano-material.
2. SrTiO of claim 13/Cu2The preparation method of the O heterojunction composite nano material is characterized in that the SrTiO in the step (5)3The molar ratio of the addition amount of the catalyst to the copper acetate in the solution is 3: 2-1: 4.
3. SrTiO of claim 13/Cu2The preparation method of the O heterojunction composite nano material is characterized in that the SrTiO in the step (5)3The molar ratio of the addition amount of the catalyst to the copper acetate in the solution is 2-1.
4. SrTiO of claim 13/Cu2The preparation method of the O heterojunction composite nanomaterial is characterized in that the molar ratio of the addition amount of glucose to copper acetate in the solution in the step (6) is 1:1-1: 1.5.
5. SrTiO of claim 13/Cu2The preparation method of the O heterojunction composite nanomaterial is characterized in that the molar ratio of titanium atoms to strontium atoms in the step (1) is 1:1.
6. SrTiO of claim 13/Cu2The preparation method of the O heterojunction composite nano material is characterized in that the concentration of the copper acetate dihydrate solution in the step (4) is 0.1 mol per liter.
7. SrTiO of claim 13/Cu2The preparation method of the O heterojunction composite nanomaterial is characterized in that the concentration of acetic acid in the step (1) is 2 mol per liter, and the concentration of citric acid is 4mol per liter.
8. SrTiO of any one of claims 1 to 73/Cu2SrTiO prepared by preparation method of O heterojunction composite nano material3/Cu2The application of the O heterojunction composite nano material in treating organic pollutants in dye wastewater.
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Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108636398B (en) * 2018-05-31 2021-04-16 武汉大学 Preparation method of vanadium-doped strontium titanate nano photocatalytic material
CN109092333B (en) * 2018-07-24 2021-08-24 江苏理工学院 Nano composite catalyst, preparation and application thereof
CN111992226B (en) * 2020-07-28 2022-12-23 南京航空航天大学 Photocatalytic nano composite catalyst and preparation method thereof
CN114984965B (en) * 2022-05-30 2023-07-21 吉林大学 P-n heterojunction composite photocatalyst Cu 2 O/MTiO 3 Preparation method and application thereof

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102643088A (en) * 2012-04-27 2012-08-22 河北师范大学 xSrTiO3-(1-x) CoFe2O4 composite material and preparation method thereof
CN102698787A (en) * 2012-06-06 2012-10-03 哈尔滨工业大学 Synthesis method of CN/SrTiO3 composite photocatalysts
CN103301846A (en) * 2013-07-11 2013-09-18 中南大学 InVO4.Cu2O.TiO2 ternary complex and preparation method and application thereof
CN103464133A (en) * 2012-06-07 2013-12-25 中国人民解放军63971部队 Preparation and chlorination method of SrTiO3/TiO2 composite photocatalyst
CN104307538A (en) * 2014-10-13 2015-01-28 东南大学 Preparation and application methods of high-efficiency composite photocatalytic material
CN104549270A (en) * 2013-10-15 2015-04-29 中国科学院金属研究所 Heterogeneous p-n knot nano composite material and preparation method and application thereof
CN105040062A (en) * 2015-07-10 2015-11-11 河海大学 Method for sensitizing TiO2 nanotube array photoelectrode through Cu2O nano particles
CN105817217A (en) * 2016-04-26 2016-08-03 武汉三江航天远方科技有限公司 SrTiO3/graphene composite catalyst as well as preparation method and application thereof
CN106732617A (en) * 2016-12-05 2017-05-31 安徽理工大学 A kind of ZnO/Cu2O hetero-junctions novel photocatalysis materials and preparation method thereof
CN107008331A (en) * 2017-04-27 2017-08-04 常州大学怀德学院 NiFe2O4/Cu2The preparation method of O magnetic composite nano catalyst and the application of the catalyst

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102643088A (en) * 2012-04-27 2012-08-22 河北师范大学 xSrTiO3-(1-x) CoFe2O4 composite material and preparation method thereof
CN102698787A (en) * 2012-06-06 2012-10-03 哈尔滨工业大学 Synthesis method of CN/SrTiO3 composite photocatalysts
CN103464133A (en) * 2012-06-07 2013-12-25 中国人民解放军63971部队 Preparation and chlorination method of SrTiO3/TiO2 composite photocatalyst
CN103301846A (en) * 2013-07-11 2013-09-18 中南大学 InVO4.Cu2O.TiO2 ternary complex and preparation method and application thereof
CN104549270A (en) * 2013-10-15 2015-04-29 中国科学院金属研究所 Heterogeneous p-n knot nano composite material and preparation method and application thereof
CN104307538A (en) * 2014-10-13 2015-01-28 东南大学 Preparation and application methods of high-efficiency composite photocatalytic material
CN105040062A (en) * 2015-07-10 2015-11-11 河海大学 Method for sensitizing TiO2 nanotube array photoelectrode through Cu2O nano particles
CN105817217A (en) * 2016-04-26 2016-08-03 武汉三江航天远方科技有限公司 SrTiO3/graphene composite catalyst as well as preparation method and application thereof
CN106732617A (en) * 2016-12-05 2017-05-31 安徽理工大学 A kind of ZnO/Cu2O hetero-junctions novel photocatalysis materials and preparation method thereof
CN107008331A (en) * 2017-04-27 2017-08-04 常州大学怀德学院 NiFe2O4/Cu2The preparation method of O magnetic composite nano catalyst and the application of the catalyst

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
Nanostructured SrTiO3 thin films sensitized by Cu2O for photoelectrochemical hydrogen generation;Dipika Sharma;《International Journal of hydrogen energy》;20140131;第4189-4197页 *

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