CN104001498A - Preparation method of zinc molybdate/graphene composite visible light catalyst - Google Patents

Preparation method of zinc molybdate/graphene composite visible light catalyst Download PDF

Info

Publication number
CN104001498A
CN104001498A CN201410247440.7A CN201410247440A CN104001498A CN 104001498 A CN104001498 A CN 104001498A CN 201410247440 A CN201410247440 A CN 201410247440A CN 104001498 A CN104001498 A CN 104001498A
Authority
CN
China
Prior art keywords
solution
water
visible light
zinc molybdate
graphene composite
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.)
Granted
Application number
CN201410247440.7A
Other languages
Chinese (zh)
Other versions
CN104001498B (en
Inventor
孙剑辉
董淑英
孙靖宇
冯精兰
皮运清
崔延瑞
苏现伐
闫旭
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.)
Henan Normal University
Original Assignee
Henan 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 Henan Normal University filed Critical Henan Normal University
Priority to CN201410247440.7A priority Critical patent/CN104001498B/en
Publication of CN104001498A publication Critical patent/CN104001498A/en
Application granted granted Critical
Publication of CN104001498B publication Critical patent/CN104001498B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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 preparation method of a zinc molybdate/graphene composite visible light catalyst. The preparation method comprises the following steps of (1) adding 2 mmol of Na2M0O4 into a graphene oxide solution, and performing ultrasonic dissolution for 30 min, so as to prepare a solution X; (2) mixing and dissolving 2mmol of Zn(CH3COO)2.2H20 into 40 ml of water, so as to obtain a transparent clear solution Y; (3) dropwise adding the solution Y into the solution X under the ultrasonic action, performing ultrasonic operation for 120 min, then adding hydrazine hydrate, uniformly mixing, and then reducing in a water bath at 80 DEG C to polymerize and precipitate, so that the solution is clear; (4) naturally cooling the solution to room temperature after reaction, filtering, washing with water and ethanol respectively for three times, and then drying in a constant-temperature drying box at 80 DEG C for 5 hours, so as to prepare the zinc molybdate/graphene composite visible light catalyst. By using the zinc molybdate/graphene composite visible light catalyst prepared with the preparation method, the light absorption can be improved. The zinc molybdate/graphene composite visible light catalyst has the advantages of wide absorption spectrum range, stable performance, no toxicity, high efficiency and cheapness, can be applied to degrading organic pollutants which are difficult to biodegrade and has a strong market application prospect.

Description

A kind of preparation method of zinc molybdate/Graphene composite visible light catalyst
Technical field
The invention belongs to visible light catalytic material technical field, be specifically related to a kind of preparation method of zinc molybdate/Graphene composite visible light catalyst that can efficient degradation rhdamine B waste water.
Background technology
Waste water from dyestuff is one of typical difficult for biological degradation organic wastewater, a large amount of dyestuffs that basicity is high, color and luster is dark, stink is large entered environment in producing and using, what wherein have also contains the carcinogens such as phenyl ring, amido, azo group, serious environment pollution, adopts conventional biological treatment removal effect not ideal enough.Nanosecond science and technology are forward position, the intercrossing new branch of science that progressively grow up in late 1980s, and it has tremendous potential at the new production technology of creation, the new aspect such as material and new product.Nano semiconductor photocatalysis oxidation technique receives publicity increasingly, especially, showing good application prospect aspect the removal of difficult for biological degradation pollutant, has become study hotspot both domestic and external.The single-phase semiconductor nano photocatalyst powder suspension system being widely studied at present, exist that nanoparticle is easily condensed, easily low, the difficult separation and recycling of inactivation, utilization ratio and the defect such as absorption spectrum ranges is narrow, seriously limited the industrial applications of nano photo catalyzed oxidation.Therefore support type, highly active composite Nano photochemical catalyst become study hotspot now.For above-mentioned defect, improved novel nano photochemical catalyst need meet the condition of three aspects: (1) can effectively stop the compound of light induced electron and hole; (2) catalyst has good adsorption capacity to pollutant; (3) catalyst cupport on suitable carrier with avoid particulate reunite.
Because Graphene has excellent electric conductivity, make it easily catch light induced electron and serve as the medium that electronics shifts, greatly strengthen the Transport Rate of electric charge, thereby can effectively stop the compound of carrier; Secondly Graphene specific area is larger, is about 2600m 2g -1, its inner aromatic structure can form π-πconjugation with pollutant, thereby shows the suction-operated strong to pollutant; Moreover Graphene has higher mechanical strength, for the deposition of catalyst provides a two-dimensional surface structure; Graphene is that a kind of energy gap is zero semimetal simultaneously, adjust its energy gap by modification, not only can realize broadband light absorption, and can also make electric charge more mate with catalyst in transfer process, improve its photocatalysis performance, so Graphene becomes the desirable material of load.
Summary of the invention
The technical problem that the present invention solves has been to provide the effectively preparation method of zinc molybdate/Graphene composite visible light catalyst of rhodamine B degradation (RhB) waste water from dyestuff of one.
Technical scheme of the present invention is: a kind of preparation method of zinc molybdate/Graphene composite visible light catalyst, it is characterized in that comprising the following steps: (1) joins the graphene oxide of 4.8-43.2mg in 40mL water, ultrasonic dispersion 60min forms graphite oxide aqueous solution, then by 2mmol Na 2moO 4join in graphite oxide aqueous solution, continue ultrasonic dissolution 30min and make solution X; (2) by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution Y; (3) under ultrasonication, solution Y is dropwise joined in solution X, continue ultrasonic 120min, add hydrazine hydrate, after stirring, be reduced to polymerization precipitation in 80 DEG C of water-baths, solution becomes clarification, and wherein often adding the quality of the corresponding graphene oxide of 1mL hydrazine hydrate is 48mg; (4) after reaction finishes, solution naturally cools to room temperature, filters, and water and ethanol are respectively washed three times, then in thermostatic drying chamber, make zinc molybdate/Graphene composite visible light catalyst in 80 DEG C of dry 5h.
Zinc molybdate/Graphene composite visible light catalyst that the present invention makes has good crystal formation and absorbing properties, and there is visible light-responded photocatalysis performance, under sunshine, there is the performance of efficient degradation rhdamine B waste water, there is absorption spectrum ranges wide, stable performance, nontoxic, efficiently cheap, can be applied to the degraded of difficult for biological degradation organic pollution, there is stronger market application foreground.
Detailed description of the invention
By the following examples foregoing of the present invention is described in further details, but this should be interpreted as to the scope of the above-mentioned theme of the present invention only limits to following embodiment, all technology realizing based on foregoing of the present invention all belong to scope of the present invention.
Embodiment 1
By 2mmol Na 2moO 4join in 40 mL water, ultrasonic dissolution 30min obtains settled solution, is designated as solution X.Meanwhile, by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution, is designated as solution Y.Then ultrasonic lower by solution Y dropwise (about 2mL/min) join in solution X, continue ultrasonic 120min.After reaction finishes, filter, water and ethanol are respectively washed three times, and then 80 DEG C of dry 5h in thermostatic drying chamber, make pure zinc molybdate photochemical catalyst.The RhB clearance of rhdamine B waste water 10h of degrading under natural sunshine is 28.4%.
Embodiment 2
0.0048g graphene oxide (GO) is joined in 40mL water to ultrasonic dispersion 60min.Then by 2mmol Na 2moO 4join in graphite oxide aqueous solution, continue ultrasonic dissolution 30min, be designated as solution X.Meanwhile, by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution, is designated as solution Y.Then ultrasonic lower by solution Y dropwise (about 2mL/min) join in solution X, continue ultrasonic 120min.Then add 0.1mL hydrazine hydrate, after stirring, proceed in thermostat water bath, 80 DEG C of water-bath reduction reaction to polymerizations precipitate, and solution becomes clarification.After reaction finishes, solution naturally cools to room temperature, filters, and water and ethanol are respectively washed three times, and then 80 DEG C of dry 5h in thermostatic drying chamber, make the zinc molybdate/Graphene composite visible light catalyst that contains 1wt% Graphene.The RhB clearance of rhdamine B waste water 10h of degrading under natural sunshine is 77.2%.
Embodiment 3
0.0144g graphene oxide is joined in 40mL water to ultrasonic dispersion 60min.Then by 2mmol Na 2moO 4join in graphite oxide aqueous solution, continue ultrasonic dissolution 30min, be designated as solution X.Meanwhile, by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution, is designated as solution Y.Then ultrasonic lower by solution Y dropwise (about 2mL/min) join in solution X, continue ultrasonic 120min.Then add 0.3mL hydrazine hydrate, after stirring, proceed in thermostat water bath, 80 DEG C of water-bath reduction reaction to polymerizations precipitate, and solution becomes clarification.After reaction finishes, solution naturally cools to room temperature, filters, and water and ethanol are respectively washed three times, and then 80 DEG C of dry 5h in thermostatic drying chamber, make the zinc molybdate/Graphene composite visible light catalyst that contains 3wt% Graphene.The RhB clearance of rhdamine B waste water 10h of degrading under natural sunshine is 96.5%.
Embodiment 4
0.024g graphene oxide is joined in 40mL water to ultrasonic dispersion 60min.Then by 2mmol Na 2moO 4join in graphite oxide aqueous solution, continue ultrasonic dissolution 30min, be designated as solution X.Meanwhile, by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution, is designated as solution Y.Then ultrasonic lower by solution Y dropwise (about 2mL/min) join in solution X, continue ultrasonic 120min.Then add 0.5mL hydrazine hydrate, after stirring, proceed in thermostat water bath, 80 DEG C of water-bath reduction reaction to polymerizations precipitate, and solution becomes clarification.After reaction finishes, solution naturally cools to room temperature, filters, and water and ethanol are respectively washed three times, and then 80 DEG C of dry 5h in thermostatic drying chamber, make the zinc molybdate/Graphene composite visible light catalyst that contains 5wt% Graphene.The RhB clearance of rhdamine B waste water 10h of degrading under natural sunshine is 84.3%.
Embodiment 5
0.0336g graphene oxide is joined in 40mL water to ultrasonic dispersion 60min.Then by 2mmol Na 2moO 4join in graphite oxide aqueous solution, continue ultrasonic dissolution 30min, be designated as solution X.Meanwhile, by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution, is designated as solution Y.Then ultrasonic lower by solution Y dropwise (about 2mL/min) join in solution X, continue ultrasonic 120min.Then add 0.7mL hydrazine hydrate, after stirring, proceed in thermostat water bath, 80 DEG C of water-bath reduction reaction to polymerizations precipitate, and solution becomes clarification.After reaction finishes, solution naturally cools to room temperature, filters, and water and ethanol are respectively washed three times, and then 80 DEG C of dry 5h in thermostatic drying chamber, make the zinc molybdate/Graphene composite visible light catalyst that contains 7wt% Graphene.The RhB clearance of rhdamine B waste water 10h of degrading under natural sunshine is 80.3%.
Embodiment 6
0.0432g graphene oxide is joined in 40mL water to ultrasonic dispersion 60min.Then by 2mmol Na 2moO 4join in graphite oxide aqueous solution, continue ultrasonic dissolution 30min, be designated as solution X.Meanwhile, by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution, is designated as solution Y.Then ultrasonic lower by solution Y dropwise (about 2mL/min) join in solution X, continue ultrasonic 120min.Then add 0.9mL hydrazine hydrate, after stirring, proceed in thermostat water bath, 80 DEG C of water-bath reduction reaction to polymerizations precipitate, and solution becomes clarification.After reaction finishes, solution naturally cools to room temperature, filters, and water and ethanol are respectively washed three times, and then 80 DEG C of dry 5h in thermostatic drying chamber, make the zinc molybdate/Graphene composite visible light catalyst that contains 9wt% Graphene.The RhB clearance of rhdamine B waste water 10h of degrading under natural sunshine is 65%.
Above embodiment has described general principle of the present invention, principal character and advantage; the technical staff of the industry should understand; the present invention is not restricted to the described embodiments; that in above-described embodiment and description, describes just illustrates principle of the present invention; do not departing under the scope of the principle of the invention; the present invention also has various changes and modifications, and these changes and improvements all fall in the scope of protection of the invention.

Claims (1)

1. the preparation method of zinc molybdate/Graphene composite visible light catalyst, it is characterized in that comprising the following steps: (1) joins the graphene oxide of 4.8-43.2mg in 40mL water, ultrasonic dispersion 60min forms graphite oxide aqueous solution, then by 2mmol Na 2moO 4join in graphite oxide aqueous solution, continue ultrasonic dissolution 30min and make solution X; (2) by 2mmol Zn (CH 3cOO) 22H 2o stirring and dissolving, in 40mL water, obtains transparent settled solution Y; (3) under ultrasonication, solution Y is dropwise joined in solution X, continue ultrasonic 120min, add hydrazine hydrate, after stirring, be reduced to polymerization precipitation in 80 DEG C of water-baths, solution becomes clarification, and wherein often adding the quality of the corresponding graphene oxide of 1mL hydrazine hydrate is 48mg; (4) after reaction finishes, solution naturally cools to room temperature, filters, and water and ethanol are respectively washed three times, then in thermostatic drying chamber, make zinc molybdate/Graphene composite visible light catalyst in 80 DEG C of dry 5h.
CN201410247440.7A 2014-06-06 2014-06-06 The preparation method of a kind of zinc molybdate/Graphene composite visible light catalyst Expired - Fee Related CN104001498B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410247440.7A CN104001498B (en) 2014-06-06 2014-06-06 The preparation method of a kind of zinc molybdate/Graphene composite visible light catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410247440.7A CN104001498B (en) 2014-06-06 2014-06-06 The preparation method of a kind of zinc molybdate/Graphene composite visible light catalyst

Publications (2)

Publication Number Publication Date
CN104001498A true CN104001498A (en) 2014-08-27
CN104001498B CN104001498B (en) 2016-06-08

Family

ID=51362574

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410247440.7A Expired - Fee Related CN104001498B (en) 2014-06-06 2014-06-06 The preparation method of a kind of zinc molybdate/Graphene composite visible light catalyst

Country Status (1)

Country Link
CN (1) CN104001498B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105591072A (en) * 2016-02-29 2016-05-18 陕西科技大学 Negative electrode piece of alpha-ZnMoO4 lithium ion battery and preparation method of negative electrode piece
CN112844368A (en) * 2021-02-18 2021-05-28 辽宁大学 ZnMOO with adjustable oxygen vacancy concentration4Photocatalyst and preparation method and application thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102580739A (en) * 2012-03-06 2012-07-18 江苏大学 Graphene/silver molybdenum oxide compound visible-light catalyst and preparation method thereof
CN102600831A (en) * 2010-06-10 2012-07-25 大连海事大学 Graphene-modified bismuth molybdate powder with high photocatalytic activity and preparation method thereof
CN103043729A (en) * 2012-12-29 2013-04-17 南京理工大学 Cobalt molybdate-graphene nano compound and preparation method thereof
CN103623809A (en) * 2013-08-27 2014-03-12 南昌航空大学 Ternary heterojunction 1%graphene-Bi2MoO6/Bi3.64Mo0.36O6.55 catalyst and preparation method thereof
CN103623803A (en) * 2012-08-30 2014-03-12 上海纳晶科技有限公司 Visible light photocatalyst and preparation method therefor
CN103811189A (en) * 2014-02-12 2014-05-21 东华大学 Preparation method of cobalt molybdate and graphene nanocomposite

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102600831A (en) * 2010-06-10 2012-07-25 大连海事大学 Graphene-modified bismuth molybdate powder with high photocatalytic activity and preparation method thereof
CN102580739A (en) * 2012-03-06 2012-07-18 江苏大学 Graphene/silver molybdenum oxide compound visible-light catalyst and preparation method thereof
CN103623803A (en) * 2012-08-30 2014-03-12 上海纳晶科技有限公司 Visible light photocatalyst and preparation method therefor
CN103043729A (en) * 2012-12-29 2013-04-17 南京理工大学 Cobalt molybdate-graphene nano compound and preparation method thereof
CN103623809A (en) * 2013-08-27 2014-03-12 南昌航空大学 Ternary heterojunction 1%graphene-Bi2MoO6/Bi3.64Mo0.36O6.55 catalyst and preparation method thereof
CN103811189A (en) * 2014-02-12 2014-05-21 东华大学 Preparation method of cobalt molybdate and graphene nanocomposite

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
SHUYING DONG 等: "ZnSnO3 hollow nanospheres/reduced graphene oxide nanocomposites as high-performance photocatalysts for degradation of metronidazole", 《APPLIED CATALYSIS B:ENVIRONMENTAL》, vol. 144, 24 July 2013 (2013-07-24) *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105591072A (en) * 2016-02-29 2016-05-18 陕西科技大学 Negative electrode piece of alpha-ZnMoO4 lithium ion battery and preparation method of negative electrode piece
CN112844368A (en) * 2021-02-18 2021-05-28 辽宁大学 ZnMOO with adjustable oxygen vacancy concentration4Photocatalyst and preparation method and application thereof
CN112844368B (en) * 2021-02-18 2023-09-15 辽宁大学 ZnMoO with adjustable oxygen vacancy concentration 4 Photocatalyst, preparation method and application thereof

Also Published As

Publication number Publication date
CN104001498B (en) 2016-06-08

Similar Documents

Publication Publication Date Title
Fan et al. Superior nanoporous graphitic carbon nitride photocatalyst coupled with CdS quantum dots for photodegradation of RhB
Wei et al. Scalable low temperature in air solid phase synthesis of porous flower-like hierarchical nanostructure SnS2 with superior performance in the adsorption and photocatalytic reduction of aqueous Cr (VI)
CN103599737B (en) One has carbon shell magnetic Nano material and preparation method
CN102350354B (en) Magnetically supported titanium dioxide photocatalyst and preparation method thereof
CN104591301B (en) A kind of porous nano CoFe 2o 4preparation method
CN106914263A (en) A kind of preparation method of composite visible light catalyst
Wang et al. Visible-light-driven double-shell SnIn4S8/TiO2 heterostructure with enhanced photocatalytic activity for MO removal and Cr (VI) cleanup
CN103007944A (en) Preparation method of graphene-based magnetic composite visible light catalysis material Fe3O4-G-TiO2
CN107098381B (en) The preparation method of the zinc titanate catalysis material of special appearance
CN108579727A (en) A kind of graphene quantum dot-bismuth tungstate composite photocatalyst and preparation method thereof
CN110575837B (en) InVO4/ZnIn2S4Photocatalyst, preparation method and application
CN105536839A (en) Method for preparing WO3/g-C3N4 composite photocatalysis material
CN104383947A (en) Silver phosphate/titanium dioxide nanocomposite and preparation method thereof
CN105502286A (en) Preparation method of porous nano NiFe2O4
CN105540640A (en) Preparation method of flower-shaped nanometer zinc oxide
CN105521789A (en) Preparation method of porous nano-scale BiFeO3
Tong et al. Preparation of carbon quantum dots/TiO2 composite and application for enhanced photodegradation of rhodamine B
CN104941662A (en) Preparation method of Ag/BFeO3 compound photocatalyst
CN104148094A (en) Preparation method of bismuth oxyfluoride/ grapheme composite visible-light-induced photocatalyst
CN104801308A (en) NiFe2O4/TiO2/sepiolite composite photocatalyst and preparation method thereof
CN107649183A (en) A kind of photochemical catalyst preparation method based on graphene
CN103551136A (en) Attapulgite loaded quasi-one-dimensional titanium dioxide composite photocatalyst and preparation method thereof
CN107892334A (en) The preparation method of nanometer alum acid iron
Basaleh et al. Novel visible light heterojunction CdS/Gd2O3 nanocomposites photocatalysts for Cr (VI) photoreduction
CN109295487A (en) The preparation of three-dimensional titanium dioxide photoelectrode for water pollutant removal

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20160608

Termination date: 20170606