CN105964250A - Ag10Si4O13 photocatalyst with visible-light response and preparation method and application thereof - Google Patents

Ag10Si4O13 photocatalyst with visible-light response and preparation method and application thereof Download PDF

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CN105964250A
CN105964250A CN201610403707.6A CN201610403707A CN105964250A CN 105964250 A CN105964250 A CN 105964250A CN 201610403707 A CN201610403707 A CN 201610403707A CN 105964250 A CN105964250 A CN 105964250A
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photocatalyst
preparation
ag10si4o13
presoma
visible
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CN105964250B (en
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黄柏标
朱相林
王朋
王泽岩
张晓阳
秦晓燕
刘媛媛
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Shandong University
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    • B01J35/61
    • 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
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/48Silver or gold
    • B01J23/50Silver
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B3/00Hydrogen; Gaseous mixtures containing hydrogen; Separation of hydrogen from mixtures containing it; Purification of hydrogen
    • C01B3/02Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen
    • C01B3/04Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen by decomposition of inorganic compounds, e.g. ammonia
    • C01B3/042Decomposition of water
    • 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
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B2203/00Integrated processes for the production of hydrogen or synthesis gas
    • C01B2203/02Processes for making hydrogen or synthesis gas
    • C01B2203/0266Processes for making hydrogen or synthesis gas containing a decomposition step
    • C01B2203/0277Processes for making hydrogen or synthesis gas containing a decomposition step containing a catalytic decomposition step
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • 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
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/30Hydrogen technology
    • Y02E60/36Hydrogen production from non-carbon containing sources, e.g. by water electrolysis
    • 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 an Ag10Si4O13 photocatalyst with visible-light response. The method includes the following steps that firstly, sodium metasilicate and silver nitrate are mixed according to the molar ratio of 1:(2-4) and evenly ground; secondly, the mixture obtained through grinding is added into deionized water and stirred, separation precipitation, washing and drying are conducted, and a precursor is obtained; thirdly, the precursor is heated to 300-500 DEG C at normal pressure and preserved for 3-5 hours, and the Ag10Si4O13 photocatalyst is obtained. Ag10Si4O13 synthesized through the method is composed of irregular nanoparticles, has high absorption in a visible light area, has high photocatalystic activity, and has the effects of decomposing water-produced oxygen through photocatalysis and degrading organic pollutants.

Description

A kind of have visible light-responded Ag10Si4O13Photocatalyst and its preparation method and application
Technical field
The present invention relates to a kind of there is visible light-responded Ag10Si4O13Photocatalyst and its preparation method and application, belongs to and partly leads Body photocatalyst technology field.
Background technology
Utilize semiconductor light-catalyst that the low-density solar energy luminous energy being difficult to collect is changed into electric energy and the change that high density easily utilizes Can become one of the most most active research field.Especially in photochemical catalyzing and utilize photooxidative degradation Unique advantage that pollutant control environment aspect shows, has caused the extensive concern of countries in the world scientist, has the most half-and-half led Body photocatalyst carries out theory and experimentation widely will have very important strategy and realistic meaning.
In all problems of the restriction actual application of photocatalysis technology at present, it is most important that how to improve the photocatalyst profit to luminous energy Use efficiency.In solar spectrum, ultraviolet light accounts for all energy 3~4%, and visible ray accounting is but more than 40%, therefore, Researching and developing visible light-responded photocatalyst is the research emphasis improving Solar use efficiency, has critically important theory And practical significance.
Silicate compound is widely used in Industrial Catalysis frequently as catalysis material, but at present about silicate compound conduct The report of photocatalyst material is less.Especially money base silicate compound, owing to its synthetic reaction condition is harsh, generally needs Wanting high oxygen press strip part, this greatly constrains the systematic study of money base silicate compound.Therefore, from silicate compound Middle discovery synthesis have the money base silicate material of high efficiency photocatalysis activity, have ten for expanding the actual application of photocatalyst Divide important meaning.
Summary of the invention
For above-mentioned prior art, it is an object of the invention to provide and a kind of there is visible light-responded Ag10Si4O13Photocatalyst and Its preparation method.
It is a further object of the present invention to provide this Ag10Si4O13Photocatalyst is at degradable organic pollutant and decomposes in Aquatic product oxygen Application.
For achieving the above object, the present invention adopts the following technical scheme that
A first aspect of the present invention, it is provided that a kind of have visible light-responded Ag10Si4O13The preparation method of photocatalyst, step As follows:
(1) by sodium metasilicate and silver nitrate 1:(2-4 in molar ratio) mixing, it is ground to uniformly;
(2) mixture that grinding obtains is joined in deionized water, stirring, precipitation separation, washing, it is dried, obtains presoma;
(3) presoma is heated to 300-500 DEG C at ambient pressure, and keeps 3-5 hour, obtain Ag10Si4O13Photocatalyst.
Preferably, in step (1), metasilicic acid is received and the mol ratio of silver nitrate is 1:3.Metasilicic acid is received and the addition of silver nitrate Amount can affect the Ag of preparation10Si4O13The structure composition of photocatalyst, the amount that metasilicic acid is received by the present invention and silver nitrate adds is carried out Investigate, it was found that metasilicic acid is received and silver nitrate 1:(2-4 in molar ratio) add and be advisable, it is possible to farthest generate mesh Mark product;Receiving when metasilicic acid adds fashionable with silver nitrate 1:3 in molar ratio, Ag10Si4O13Productivity the highest.
Preferably, in step (1), milling time is 15-25min, further, and preferably 20min.Permissible by grinding Improve the contact situation of reactant in the solid state reaction of the present invention, to increase the defect density being conducive to reaction, improve reaction Thermodynamics and kinetics condition, enables solid state reaction to be smoothed out.Milling time is optimized by the present invention, it was found that If milling time is too short, then reactant is insufficient contact;If milling time is long, then on the one hand extend generated time, increase Add production cost, on the other hand also may can affect the crystal configuration of product.Find through multiple comparison test, during grinding Between be advisable with 15-25min.
Preferably, in step (2), the ratio grinding mixture and the deionized water addition obtained is (0.5-1.5) mmol: 10ml。
Preferably, in step (2), washing uses deionized water and washes of absolute alcohol.
Preferably, in step (3), presoma is heated at ambient pressure 400 DEG C.Presoma is carried out heat treatment can change The crystal phase structure of product, and the crystal phase structure of product is closely related with its photocatalytic activity, heat treatment temperature is carried out by the present invention Investigate, it was found that the temperature of heat treatment higher than 500 DEG C or all cannot generate the crystalline A g of the present invention less than 300 DEG C10Si4O13
Preferably, in step (3), carry out being warming up to heating-up temperature with the speed of 5 DEG C/min.
Ag prepared by said method10Si4O13Photocatalyst, is made up of random nano-particle, at transition metal ions (Ag+) In the presence of, the SiO in silicate4Tetrahedron easily distorts and produces polarization, by controlling the tetrahedral arrangement meeting of these polarity An internal polarization electric field is built at material internal;It addition, the coordination environment of the transition metal of complexity is that light induced electron is connected many Transfer between the body of face provides probability.Therefore, the Ag that prepared by said method10Si4O13There is high efficiency photocatalysis activity.
A second aspect of the present invention, it is provided that above-mentioned Ag10Si4O13Photocatalyst is in decomposing Aquatic product oxygen and degradable organic pollutant Application.
Beneficial effects of the present invention:
(1) Ag prepared by the present invention10Si4O13Photocatalyst has visible light-responded, through experimental studies have found that, and Ag10Si4O13 Demonstrate preferable photocatalytic activity, under visible ray shines, decompose Aquatic product oxygen 110umol at 2.5 hours, degraded 98% in 50 minutes Methylene blue organic dyestuff.Under full light (300nm-1100nm), its photooxidative degradation methylene blue efficiency is than commodity TiO2 (P25) more outstanding.Therefore, the Ag that prepared by the present invention10Si4O13Photocatalyst has decomposition Aquatic product oxygen and degraded sky simultaneously The double effects of gas, waste water, surface water or Organic Pollutants of Drinking Water, this is the money base silicate compound institute of existing report Do not possess.
(2) Ag of the present invention10Si4O13Photocatalyst uses solid state reaction kinetics, is initially formed presoma, then through room temperature, height Temperature solid state reaction crystallization, forms thermodynamically stable Ag10Si4O13Crystal.Preparation synthetic method condition is simple, it is not necessary to high Oxygen press strip part, it is not necessary to add organic solvent, reaction condition is gentle, is more suitable for large-scale production and actual application, has higher Commercial applications prospect.
Accompanying drawing explanation
Fig. 1 is presoma of the present invention, crystalline A g10Si4O13The X ray picture of standard card;
Fig. 2 is the optical absorption map of product of the present invention;
Fig. 3 is the SEM figure of product of the present invention;
Fig. 4 is that the embodiment of the present invention product photocatalyst and the N doping P25 that are formed are for Photocatalytic Activity for Degradation organic dyestuff Methylene blue contrasts;
Fig. 5 is total carbon content (TC) in solution before and after photocatalyst Photocatalytic Activity for Degradation organic dyestuff methylene blue, organic Carbon content (TOC) and inorganic carbon amounts (IC) variation diagram;
Fig. 6 is that the photocatalyst of embodiment of the present invention product formation is for photocatalysis Decomposition Aquatic product oxygen yield figure.
Detailed description of the invention
The present invention is further illustrated in conjunction with the embodiments, it should explanation, following embodiment merely to explain the present invention, Its content is not defined.
Embodiment 1:
Weigh 3mmol sodium metasilicate and 9mmol silver nitrate is put in agate mortar, grind 20 minutes until color even.So After uniform for grinding mixture is all poured in 100mL beaker, add 100mL deionized water stir ten minutes.Finally will Precipitate and separate with deionized water and washes of absolute alcohol, is finally being dried at room temperature for, i.e. can get presoma.
The precursor powder of gained is placed in crucible, is then heated to 400 degrees Celsius with the speed of 5 degrees Celsius per minute and protects Hold 4 hours, carry out secondary solid-phase heat treatment, i.e. obtain the Ag that crystallinity is good10Si4O13
Presoma and crystalline A g to preparation10Si4O13Carry out structural characterization and performance test, wherein, presoma and crystallization Ag10Si4O13X-ray diffractogram as shown in Figure 1;Crystalline A g10Si4O13Optical absorption map as shown in Figure 2;Crystallization Ag10Si4O13SEM scheme as shown in Figure 3.
As seen from Figure 1, it is essentially amorphous phase without the presoma of heat treatment, after 4 hours heat treatments, product Showing preferable crystallinity, composition is Ag10Si4O13, obvious miscellaneous peak does not occur.As seen from Figure 2, crystallization Ag10Si4O13The strongest absorption is had at visible regime.As seen from Figure 3, the Ag that the present embodiment obtains10Si4O13Product is The granule of 2 microns, the most special pattern.
Embodiment 2:
Weigh 3mmol sodium metasilicate and 6mmol silver nitrate is put in agate mortar, grind 20 minutes until color even.So After uniform for grinding mixture is all poured in 100mL beaker, add 100mL deionized water stir ten minutes.Finally will Precipitate and separate with deionized water and washes of absolute alcohol, is finally being dried at room temperature for, i.e. can get presoma.
The precursor powder of gained is placed in crucible, is then heated to 300 degrees Celsius with the speed of 5 degrees Celsius per minute and protects Hold 3 hours, carry out secondary solid-phase heat treatment, i.e. obtain the Ag that crystallinity is good10Si4O13
Embodiment 3:
Weigh 3mmol sodium metasilicate and 12mmol silver nitrate is put in agate mortar, grind 20 minutes until color even. Then uniform for grinding mixture is all poured in 100mL beaker, add 100mL deionized water and stir ten minutes.Finally By precipitate and separate and with deionized water and washes of absolute alcohol, finally it is being dried at room temperature for, i.e. can get presoma.
The precursor powder of gained is placed in crucible, is then heated to 500 degrees Celsius with the speed of 5 degrees Celsius per minute and protects Hold 5 hours, carry out secondary solid-phase heat treatment, i.e. obtain the Ag that crystallinity is good10Si4O13
Performance test:
1. photocatalytically degradating organic dye test
Common 100mL glass beaker is carried out under normal temperature and pressure.Light source selects the 300W xenon lamp equipped with optical filter so that Optical source wavelength is more than 420nm.The photocatalytic activity of sample is evaluated with methylene blue.Weigh 50mg germne sample dispersion 50 In ml methylene blue B solution (20mg/L).Before light-catalyzed reaction test, lucifuge magnetic agitation 30min makes methylene blue in catalysis Agent surface reaches adsorption equilibrium, samples 3ml, centrifugation every 10min, take supernatant UV, visible light spectrophotometric after logical light Measurement amount absorbance.
The crystalline A g of embodiment 1 preparation10Si4O13Photocatalytically degradating organic dye test result as illustrated in figures 4-5, as seen from the figure, Photocatalyst is tested through photocatalytically degradating organic dye methylene blue under visible light, and photocatalyst can be at 50 minutes by methylene blue Degraded 98%, its photocatalytic activity is higher than N doping P25.
2. photocatalysis Decomposition Aquatic product oxygen test
The glass container system having recirculated cooling water (5 DEG C) to close in connection carries out and carries out, and vacuum condition is-97KPa.At top The light source irradiated selects the 300W xenon lamp equipped with optical filter so that optical source wavelength is more than 420nm.Enter every 0.5h after logical light Row test, gas chromatograph the peak area value recorded is converted into the yield of oxygen.
The crystalline A g of embodiment 1 preparation10Si4O13Photocatalysis Decomposition Aquatic product oxygen result as shown in Figure 6, Fig. 6 can see Going out, photocatalyst can produce about 110umol oxygen by decomposition water in 2.5h under visible light.
Above detection and analysis integrated demonstrate the product that the present invention obtains and have visible light-responded for Photocatalyzed Hydrogen Production Photocatalyst.And in terms of light degradation organic pollution and decomposition Aquatic product oxygen, there is preferable using value.

Claims (10)

1. one kind has visible light-responded Ag10Si4O13The preparation method of photocatalyst, it is characterised in that step is as follows:
(1) by sodium metasilicate and silver nitrate 1:(2-4 in molar ratio) mixing, it is ground to uniformly;
(2) mixture that grinding obtains is joined in deionized water, stirring, precipitation separation, washing, it is dried, obtains presoma;
(3) presoma is heated to 300-500 DEG C at ambient pressure, and keeps 3-5 hour, obtain Ag10Si4O13Photocatalyst.
2. preparation method as claimed in claim 1, it is characterised in that in step (1), metasilicic acid is received and the rubbing of silver nitrate That ratio is 1:3.
3. preparation method as claimed in claim 1, it is characterised in that in step (1), milling time is 15-25min; It is preferably 20min.
4. preparation method as claimed in claim 1, it is characterised in that in step (2), grinds the mixture that obtains and goes The ratio of ionized water addition is (0.5-1.5) mmol:10ml.
5. preparation method as claimed in claim 1, it is characterised in that in step (2), washing uses deionized water And washes of absolute alcohol.
6. preparation method as claimed in claim 1, it is characterised in that in step (3), presoma is heated at ambient pressure To 400 DEG C.
7. preparation method as claimed in claim 1, it is characterised in that in step (3), rise with the speed of 5 DEG C/min Temperature is to heating-up temperature.
8. the Ag that the preparation method described in any one of claim 1-7 prepares10Si4O13Photocatalyst.
9. the Ag described in claim 810Si4O13Photocatalyst purposes in degradable organic pollutant.
10. the Ag described in claim 810Si4O13Photocatalyst purposes in decomposing Aquatic product oxygen.
CN201610403707.6A 2016-06-08 2016-06-08 It is a kind of with visible light-responded Ag10Si4O13Photochemical catalyst and its preparation method and application Active CN105964250B (en)

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CN109395724A (en) * 2018-11-09 2019-03-01 南通大学 A kind of disilicic acid silver-TiO 2 visible light catalyst and preparation method thereof
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CN107020091A (en) * 2017-03-27 2017-08-08 山东大学 It is a kind of that there is visible light-responded Ag4(GeO4) photochemical catalyst and its preparation method and application
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CN109126783A (en) * 2018-08-20 2019-01-04 盐城工学院 A kind of disilicic acid silver/carbon nanotube visible-light photocatalyst and preparation method thereof
CN109395724A (en) * 2018-11-09 2019-03-01 南通大学 A kind of disilicic acid silver-TiO 2 visible light catalyst and preparation method thereof
CN109647382A (en) * 2019-01-28 2019-04-19 兰州理工大学 A kind of macropore silver silicate photochemical catalyst and the preparation method and application thereof
CN109647383A (en) * 2019-01-28 2019-04-19 兰州理工大学 A kind of nanometer of silver silicate photochemical catalyst and the preparation method and application thereof
CN109794238A (en) * 2019-01-28 2019-05-24 兰州理工大学 A kind of rGO/ silver silicate composite material and preparation method and application
CN114150153A (en) * 2021-11-03 2022-03-08 深圳市世清环保科技有限公司 Method for recycling silver-containing waste nitric acid and recovering silver

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