CN108079993B - Preparation method of ferrous oxide/cuprous oxide nano composite material - Google Patents

Preparation method of ferrous oxide/cuprous oxide nano composite material Download PDF

Info

Publication number
CN108079993B
CN108079993B CN201711444507.6A CN201711444507A CN108079993B CN 108079993 B CN108079993 B CN 108079993B CN 201711444507 A CN201711444507 A CN 201711444507A CN 108079993 B CN108079993 B CN 108079993B
Authority
CN
China
Prior art keywords
copper
composite material
preparation
cuprous oxide
oxide
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201711444507.6A
Other languages
Chinese (zh)
Other versions
CN108079993A (en
Inventor
张建
刘国栋
吴思奇
毕旺杰
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.)
Shandong Copolymer Silicone Technology Research Institute Co ltd
Original Assignee
Jining 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 Jining University filed Critical Jining University
Priority to CN201711444507.6A priority Critical patent/CN108079993B/en
Publication of CN108079993A publication Critical patent/CN108079993A/en
Application granted granted Critical
Publication of CN108079993B publication Critical patent/CN108079993B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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
    • B01J23/74Iron group metals
    • B01J23/745Iron
    • 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
    • B82NANOTECHNOLOGY
    • B82YSPECIFIC USES OR APPLICATIONS OF NANOSTRUCTURES; MEASUREMENT OR ANALYSIS OF NANOSTRUCTURES; MANUFACTURE OR TREATMENT OF NANOSTRUCTURES
    • B82Y30/00Nanotechnology for materials or surface science, e.g. nanocomposites
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B82NANOTECHNOLOGY
    • B82YSPECIFIC USES OR APPLICATIONS OF NANOSTRUCTURES; MEASUREMENT OR ANALYSIS OF NANOSTRUCTURES; MANUFACTURE OR TREATMENT OF NANOSTRUCTURES
    • B82Y40/00Manufacture or treatment of nanostructures
    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent

Abstract

The invention relates to a preparation method of a ferrous oxide/cuprous oxide nano composite material, belonging to the technical field of inorganic material preparation, wherein ferric salt is dissolved in water to obtain a ferric salt solution; adding metal copper into the ferric salt solution, and continuously stirring for 5-30 min; putting the solution into a reaction kettle, and reacting at the temperature of 80-150 ℃ for 0.5-8 h; washing the product obtained in the step 3) with a detergent for 1-3 times, and drying at the temperature of 0-120 ℃ for 2-12 h. The invention can prepare the ferrous oxide/cuprous oxide composite nano material by one step by using a simple one-step low-temperature hydrothermal method without adding an organic solvent, the particles and the components are controllable, the cost is low, and the problems of complex preparation process and high cost of the composite material are solved; the preparation method is simple and convenient, has no harm to the environment, is suitable for large-scale industrial production, and has wide application prospect; the obtained product has excellent performance, can be used as a Fenton reaction reagent, can show excellent catalytic performance at neutral pH value, normal temperature and sunlight, and has enhanced catalytic activity and improved structural stability.

Description

Preparation method of ferrous oxide/cuprous oxide nano composite material
Technical Field
The invention belongs to the technical field of inorganic material preparation, and particularly relates to a preparation method of a ferrous oxide/cuprous oxide nano composite material.
Background
With the rapid development of human society, the shortage of energy and environmental pollution threaten the survival of human beings more and more. At present, organic wastewater has the defects of difficult biodegradation, high toxicity and difficult degradation by a traditional method. After long-term efforts, many methods for purifying sewage have been established, such as physical adsorption, chemical reaction and biodegradation, but the treatment of organic pollutants in sewage still has the disadvantages of incomplete degradation, high catalyst cost, large dosage, high cost and the like. With the enhancement of environmental protection in the world and countries, there is a need to explore efficient, harmless and novel catalyst materials.
Among a plurality of catalyst materials, a photocatalyst for degrading organic pollution in water by utilizing sunlight becomes an effective method and is more and more paid attention to by people. The light Fenton reaction is one of advanced oxidation technologies, light energy is used as drive, active groups with strong oxidizing property generated by catalyzing hydrogen peroxide by iron ions can completely degrade organic pollutants in water to form carbon dioxide, water, inorganic salt and the like which are harmless to the environment, and the method has the advantages of low price, convenience, harmlessness to the environment, easiness in industrialization and the like, and is concerned. Cuprous oxide is a typical p-type semiconductor, has unique optical properties, can initiate a photocatalytic reaction under sunlight, and has attracted the attention of numerous researchers. At present, some methods for preparing cuprous oxide materials have been tried, for example, the patent of the invention (CN107162038A) reports a method for preparing cuprous oxide by using an aerosol method; the invention patent (CN106423166A) reports a method for preparing cuprous oxide using organic reducing agent; the invention patent (CN105836787A) reports a method for preparing cuprous oxide by using organic alkylamine. But also has the defects of complex preparation process and high organic matter content and is difficult to remove, thereby greatly increasing the cost of the product. At the same time, ferrous oxide also exhibits very excellent effects as a fenton reagent. The single metal oxide still can not meet the requirements of practical application, and the composite catalyst can solve the defects of a single-component catalyst, so that the ferrous oxide/cuprous oxide-based composite material has more excellent performance than single cuprous oxide or ferrous oxide. The preparation of the ferrous oxide/cuprous oxide composite nano material by using simple and cheap raw materials and a simple one-step method becomes a difficult point in scientific research and production application at present.
Disclosure of Invention
The invention aims to provide a preparation method of a ferrous oxide/cuprous oxide nanocomposite, the ferrous oxide/cuprous oxide nanocomposite is prepared by a simple one-step low-temperature hydrothermal method, the particle size and composition of particles of a composite structure are controllable, the catalytic performance and the structural stability are improved, and the preparation method is simple in process flow, low in cost and suitable for large-scale production.
In order to achieve the purpose, the invention adopts the technical scheme that:
the preparation method of the ferrous oxide/cuprous oxide nano composite material takes ferric salt and metallic copper as raw materials, and prepares the composite material with controllable composition and particle size by using redox reaction between the ferric salt and the metallic copper and a one-step low-temperature hydrothermal method.
The preparation method of the ferrous oxide/cuprous oxide nanocomposite material comprises the following steps:
1) dissolving iron salt in water to obtain iron salt solution, and controlling concentration to be 2.5 x 10-3-7.5*10-2mol/L;
2) Adding metal copper into the ferric salt solution, and continuously stirring for 5-30 min;
3) putting the solution into a reaction kettle, and reacting at the temperature of 80-150 ℃ for 0.5-8 h;
4) washing the product obtained in the step 3) with a detergent for 1-3 times, and drying at the temperature of 0-120 ℃ for 2-12 h.
The iron salt is one or more of ferric chloride, ferric nitrate or ferric sulfate.
The metal copper is one or more of copper powder, copper sheet or foam copper.
Controlling the amount of iron ions on the copper metal to be 1 x 10-5mol/cm2-3*10-4mol/cm2
The detergent in the step 4) is water, ethanol or acetone.
The invention has the beneficial effects that:
(1) the invention can prepare the ferrous oxide/cuprous oxide composite nano material by one step by using a simple one-step low-temperature hydrothermal method without adding an organic solvent, has controllable particles and components and low cost, and solves the problems of complex preparation process and high cost of the composite material.
(2) The preparation method is simple and convenient, has no harm to the environment, is suitable for large-scale industrial production, and has wide application prospect.
(3) The prepared ferrous oxide/cuprous oxide composite nano material has excellent performance, can show excellent catalytic performance at neutral pH value, normal temperature and sunlight as a Fenton reaction reagent, and has enhanced catalytic activity and improved structural stability.
Drawings
FIG. 1 is the XRD pattern of ferrous/cuprous oxide in example 1;
FIG. 2 is an SEM image of ferrous/cuprous oxide in example 1;
FIG. 3 is a graph showing the degradation of the dye molecules in example 1.
Detailed Description
The present invention is further illustrated by, but not limited to, the following examples.
The degradation product is 5mg/L of methylene blue and rhodamine B dye mixed solution (each accounts for 50 wt%).
Example 1
The preparation method of the ferrous oxide/cuprous oxide nanocomposite comprises the steps of dissolving ferric trichloride in water, wherein the concentration of the ferric trichloride is 0.01 mol/L; adding a metal copper sheet into the ferric trichloride solution, and continuously stirring for 15 minutes, wherein the amount of iron ions on the copper sheet is 1 x 10-4mol/cm2Then the mixture is put into a reaction kettle to react for 5 hours at the temperature of 100 ℃; the resulting product was washed 3 times with ethanol and dried at 90 ℃ for 8 hours.
The diffraction pattern of the crystal structure of fig. 1 shows that the product is a ferrous oxide/cuprous oxide composite material. As can be seen from fig. 2, the composite nanostructure of ferrous oxide/cuprous oxide is spherical particles with an average particle size of about 80 nm. 0.05g of ferrous oxide/cuprous oxide composite material is added into 100mL of mixed solution of methylene blue and rhodamine B dye (the concentration is 5mg/L), stirred for 40min in the dark, and then added with 0.5mL of hydrogen peroxide (the concentration is 30 wt%) for degradation experiment. As shown in the degradation of rhodamine B in FIG. 3, the ferrous oxide/cuprous oxide composite material can completely degrade organic pollutants within 30 min.
Example 2
As described in example 1, except that iron nitrate was added. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 90 nanometers, and the degradation of organic matters reaches 100 percent within 30 minutes.
Example 3
As described in example 1, except that iron sulfate was added. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 100 nanometers, and the degradation of organic matters reaches 100 percent in 30 min.
Example 4
As described in example 1, except that the concentration of the iron trichloride solution was 0.005 mol/L. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 75 nanometers, and the degradation of organic matters reaches 100 percent in 30 min.
Example 5
As described in example 1, except that the concentration of the iron trichloride solution was 0.05 mol/L. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 110 nanometers, and the degradation of organic matters reaches 95 percent in 30 min.
Example 6
Except that copper foam was added as described in example 1. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 60 nanometers, and the degradation of organic matters reaches 100 percent in 30 min.
Example 7
Except that copper foam was added as described in example 1. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 65 nanometers, and the degradation of organic matters reaches 100 percent in 30 min.
Example 8
As described in example 1, except that the amount of iron ions on the copper sheet was 2 x 10-5mol/cm2. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 70 nanometers, and the degradation of organic matters reaches 100 percent in 30 min.
Example 9
The reaction was carried out in a reaction vessel at 80 ℃ for 7 hours, as described in example 1. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 65 nanometers, and the degradation of organic matters reaches 100 percent in 30 min.
Example 10
The reaction was carried out in a reaction vessel at 140 ℃ for 3 hours, as described in example 1. The average grain diameter of the obtained ferrous oxide/cuprous oxide composite material is 95 nanometers, and the degradation of organic matters reaches 100 percent in 30 min.

Claims (4)

1. A preparation method of a ferrous oxide/cuprous oxide nano composite material is characterized in that ferric salt and metallic copper are used as raw materials, and a composite material with controllable composition and particle size is prepared by using an oxidation-reduction reaction between the ferric salt and the metallic copper and a one-step low-temperature hydrothermal method; the method specifically comprises the following steps:
1) dissolving iron salt in water to obtain iron salt solution with concentration of 2.5 × 10-3-7.5×10-2mol/L;
2) Adding metal copper into the ferric salt solution, and continuously stirring for 5-30 min;
3) putting the solution into a reaction kettle, and reacting at the temperature of 80-150 ℃ for 0.5-8 h;
4) washing the product obtained in the step 3) with a detergent for 1-3 times, and drying at the temperature of 0-120 ℃ for 2-12 h;
in the step 2), the amount of iron ions on the metal copper is controlled to be 1 multiplied by 10-5mol/cm2-3×10-4mol/cm2
2. The method of claim 1, wherein the ferric salt is one or more of ferric chloride, ferric nitrate, or ferric sulfate.
3. The method of claim 1, wherein the copper metal is one or a combination of copper powder, copper flakes, or copper foam.
4. The method for preparing ferrous oxide/cuprous oxide nanocomposite as claimed in claim 1, wherein said detergent in step 4) is water, ethanol or acetone.
CN201711444507.6A 2017-12-27 2017-12-27 Preparation method of ferrous oxide/cuprous oxide nano composite material Active CN108079993B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201711444507.6A CN108079993B (en) 2017-12-27 2017-12-27 Preparation method of ferrous oxide/cuprous oxide nano composite material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201711444507.6A CN108079993B (en) 2017-12-27 2017-12-27 Preparation method of ferrous oxide/cuprous oxide nano composite material

Publications (2)

Publication Number Publication Date
CN108079993A CN108079993A (en) 2018-05-29
CN108079993B true CN108079993B (en) 2021-01-05

Family

ID=62179681

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201711444507.6A Active CN108079993B (en) 2017-12-27 2017-12-27 Preparation method of ferrous oxide/cuprous oxide nano composite material

Country Status (1)

Country Link
CN (1) CN108079993B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111193012B (en) * 2020-01-08 2021-02-19 四川大学 Hollow porous cuprous oxide-cupric oxide-ferric oxide cubic lithium ion battery cathode and one-step preparation method thereof
CN111135830A (en) * 2020-01-14 2020-05-12 江苏海洋大学 Simple and green preparation method and application of micro-nano powder with copper and cuprous oxide composite structure
CN113769742B (en) * 2021-07-28 2023-11-17 同济大学 Copper mesh integrated Cu 2 Preparation method of O@FeO nano array
CN115072856A (en) * 2022-04-27 2022-09-20 赣南医学院 Application of copper-iron-oxygen nanoenzyme in removing colored printing and dyeing dye and kit for removing printing and dyeing dye

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6673738B2 (en) * 2001-11-28 2004-01-06 K.K. Ueda Shikimono Kojyo Photocatalytic active carbon, colored photocatalytic active carbon, coloring active carbon, and deodorant and adsorption product using them
CN101204652A (en) * 2007-12-19 2008-06-25 中国科学院上海硅酸盐研究所 High efficiency semiconductor photocatalysis and preparation method thereof
CN104001519A (en) * 2014-06-12 2014-08-27 淮北师范大学 Method for preparing Cu2O/Bi2O3 nanometer compound photocatalysts in indoor temperature solid-phase one-step mode
CN105312055A (en) * 2015-11-26 2016-02-10 江苏大学 Preparation method and application of Fenton-like catalyst

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6673738B2 (en) * 2001-11-28 2004-01-06 K.K. Ueda Shikimono Kojyo Photocatalytic active carbon, colored photocatalytic active carbon, coloring active carbon, and deodorant and adsorption product using them
CN101204652A (en) * 2007-12-19 2008-06-25 中国科学院上海硅酸盐研究所 High efficiency semiconductor photocatalysis and preparation method thereof
CN104001519A (en) * 2014-06-12 2014-08-27 淮北师范大学 Method for preparing Cu2O/Bi2O3 nanometer compound photocatalysts in indoor temperature solid-phase one-step mode
CN105312055A (en) * 2015-11-26 2016-02-10 江苏大学 Preparation method and application of Fenton-like catalyst

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
几种铜基可见光催化剂的制备及其光催化性能的研究;冯晨;《中国优秀硕士学位论文全文数据库 工程科技I辑》;20140915(第 9 期);第53页第5.2.2节、第66页第6.2.2节 *

Also Published As

Publication number Publication date
CN108079993A (en) 2018-05-29

Similar Documents

Publication Publication Date Title
Yu et al. Enhanced photocatalytic tetracycline degradation using N-CQDs/OV-BiOBr composites: Unraveling the complementary effects between N-CQDs and oxygen vacancy
Lan et al. Application of polyoxometalates in photocatalytic degradation of organic pollutants
CN108675430B (en) Catalytic process for the production of sulfate radicals and reactive oxygen species and advanced oxidation of nonbiodegradable organic pollutants
CN108079993B (en) Preparation method of ferrous oxide/cuprous oxide nano composite material
CN102580742B (en) Activated carbon-loaded cuprous oxide photocatalyst and preparation method thereof
Xu et al. Visible light-degradation of azo dye methyl orange using TiO2/β-FeOOH as a heterogeneous photo-Fenton-like catalyst
Salari et al. Fabrication of novel Fe2O3/MoO3/AgBr nanocomposites with enhanced photocatalytic activity under visible light irradiation for organic pollutant degradation
Qu et al. Controllable synthesis of a sponge-like Z-scheme N, S-CQDs/Bi2MoO6@ TiO2 film with enhanced photocatalytic and antimicrobial activity under visible/NIR light irradiation
Guan et al. Synthesis and characterization of ZnO@ RSDBC composites and their Photo-Oxidative degradation of Acid Orange 7 in water
Zhang et al. Construction of plasmonic Bi/Bismuth oxycarbonate/Zinc bismuth oxide ternary heterojunction for enhanced charge carrier separation and photocatalytic performances
CN113908878B (en) Preparation method and application of bimetallic Prussian blue analogue catalyst
Xie et al. In situ-generated H2O2 with NCQDs/MIL-101 (Fe) by activating O2: A dual effect of photocatalysis and photo-Fenton for efficient removal of tetracyline at natural pH
Kan et al. Glycol assisted splitting BiOIO3 into plasmonic bismuth coupled with BiOI co-modified Bi2WO6 (BiOI/Bi/Bi2WO6) to form indirect Z-scheme heterojunction for efficient photocatalytic degradation of BPA
Hu et al. Facile synthesis of Z-scheme Bi2O3/Bi2WO6 composite for highly effective visible-light-driven photocatalytic degradation of nitrobenzene
CN112142097B (en) Cadmium stannate trihydrate, and preparation method and application thereof
Liu et al. Metal-organic frameworks derived TiO2/carbon nitride heterojunction photocatalyst with efficient catalytic performance under visible light
Yang et al. Two-dimensional layered organic hybrid selenidostannate coupled with polyaniline for high efficient photocatalytic Cr (VI) reduction
Dou et al. Ag nanoparticle-decorated 2D/2D S-scheme gC 3 N 4/Bi 2 WO 6 heterostructures for an efficient photocatalytic degradation of tetracycline
Tang et al. A novel S-scheme heterojunction in spent battery-derived ZnFe2O4/g-C3N4 photocatalyst for enhancing peroxymonosulfate activation and visible light degradation of organic pollutant
Bai et al. Wet chemical synthesis of CdS/ZnO nanoparticle/nanorod hetero-structure for enhanced visible light disposal of Cr (VI) and methylene blue
Chen et al. Efficient degradation of ciprofloxacin by Cu2O/g-C3N4 heterostructures with different morphologies driven under the visible light
Wu et al. Heterogeneous catalytic system of photocatalytic persulfate activation by novel Bi2WO6 coupled magnetic biochar for degradation of ciprofloxacin
Prabhavathy et al. Visible light-induced Silver and Lanthanum co-doped BiVO4 nanoparticles for photocatalytic dye degradation of organic pollutants
Dagar et al. Photo-degradation of methyl orange under visible light by PEDOT/NiO/Fly ash cenosphere
Wang et al. ZnS quantum dots implanted polyaniline-wrapped corn straw catalysts for efficient photocatalytic nitrate reduction without external addition of hole scavengers

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20240112

Address after: 262600 No. 008, Ying Long Road, Longshan hi tech Industrial Park, Linqu, Weifang, Shandong

Patentee after: Shandong copolymer silicone Technology Research Institute Co.,Ltd.

Address before: No.16 Haichuan Road, Jining high tech Zone, Shandong Province, 272001

Patentee before: JINING University