CN106745481A - One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups - Google Patents

One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups Download PDF

Info

Publication number
CN106745481A
CN106745481A CN201611206949.2A CN201611206949A CN106745481A CN 106745481 A CN106745481 A CN 106745481A CN 201611206949 A CN201611206949 A CN 201611206949A CN 106745481 A CN106745481 A CN 106745481A
Authority
CN
China
Prior art keywords
graphene
continuous
quartz plate
secondary groups
loaded
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.)
Pending
Application number
CN201611206949.2A
Other languages
Chinese (zh)
Inventor
王铀
张迪
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.)
Harbin Institute of Technology
Original Assignee
Harbin Institute of Technology
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 Harbin Institute of Technology filed Critical Harbin Institute of Technology
Priority to CN201611206949.2A priority Critical patent/CN106745481A/en
Publication of CN106745481A publication Critical patent/CN106745481A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/18Carbon
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/58Fabrics or filaments
    • B01J35/59Membranes
    • 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
    • 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
    • C02F2305/02Specific form of oxidant
    • C02F2305/023Reactive oxygen species, singlet oxygen, OH radical
    • 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
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Catalysts (AREA)

Abstract

One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups.The present invention relates to the continuous photocatalysis method that one kind fills Graphene/P25 laminated films based on secondary groups.The present invention is disposed waste liquid to solve the problems, such as that existing batch (-type) handling process cannot meet big commercial scale.Method:First, quartz plate upper strata connects layer (LbL) Technical form Graphene/P25 multilayer films (one-level assembling);2nd, the quartz plate assembly array (secondary groups dress) of Graphene/P25 multilayer films is loaded;3rd, continuous photocatalytic degradation technique.The present invention prepares brand-new Graphene/P25 layers and connects a layer laminated film array using secondary groups dress technology, using pump circulation fluid, effectively realizes continuous photocatalytically degradating organic dye, is adapted to scale sewage disposal.Catalyst is carried on quartz plate, technological operation is greatly simplified, has both solved the problems, such as that catalyst reclaims difficult, photocatalysis efficiency is improve again, it is adaptable to high-volume sewage disposal.

Description

One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups
Technical field
The present invention relates to one kind based on secondary groups dress Graphene/P25 (commercial TiO2) laminated film continuous photocatalysis side Method.
Background technology
In recent years, continuing to develop with industry, effectively utilizes and environmental protection to regenerative resource, the water resource of cleaning What is become is increasingly important, the major issue as mankind institute urgent need to resolve.For example:Printing and dyeing are developed rapidly to water with textile industry The pollution that body is caused is increasingly severe.Therefore, how to eliminate pollution, reducing energy consumption by effective means is that current science is ground Study carefully the significant challenge for facing.In numerous wastewater processing technologies, using the Photocatalyst of solar energy be a kind of row it Can solve effectively and simultaneously the means that the world today faces energy shortage and the hang-up of environmental pollution two.
Conventional conductor photocatalysis material includes TiO2、Fe2O3、ZnS、MoS2、WO3With CdS etc..TiO2Because its is excellent Photocatalysis performance, good stability, it is nontoxic, cheap the advantages of, more broadly ground in numerous catalysis materials Study carefully and apply.However, the semiconductor light-catalyst of most of reported in literature is the powder catalyst of nano-scale at present, use Be batch (-type) handling process.During using this technique photocatalytic degradation, powder photocatalyst need to be directly dispersing in target dyestuff In solution, degraded in a kettle. under conditions of continuously stirring, catalyst is passed through into centrifugation after degraded terminates Out preparing for the next use.But actually this batch (-type) handling process cannot meet what big commercial scale disposed waste liquid at all It is required that:One side liquid agitation amount is big, and required reactor volume is big, quantity is more and stirs huge energy consumption;Above all receive It is difficult to be separated with the liquid that is degraded after the completion of the powder catalyst light degradation of metrical scale, causes the batch (-type) light based on powder catalyst Degradation technique rests on laboratory stage always for a long time, it is difficult to put into production application.Therefore, exploitation is new without separating Type photochemical catalyst, the continuous light degradation technology generations implemented in being flowed with liquid are photocatalysis technologies for interval batch processing degradation technique Move towards the key of scale practical application.On the other hand, TiO2Used as catalysis material, haveing the shortcomings that can be wide with band gap, leads The electronics that cause plays a decisive role to photocatalysis efficiency and hole low yield (electron-hole separates hardly possible, is easily combined after separation), seriously Have impact on TiO2The disposal efficiency of catalysis material.
The content of the invention
The present invention is disposed waste liquid to solve the problems, such as that existing batch (-type) handling process cannot meet big commercial scale, and The continuous photocatalysis method of Graphene/P25 laminated films is filled based on secondary groups there is provided one kind.
Continuous photocatalysis method of the one kind based on secondary groups dress Graphene/P25 laminated films specifically enters according to the following steps Capable:
First, a layer Technical form Graphene/P25 multilayer films are connect using layer on quartz plate:P25 is dispersed in the salt that pH is 2 In acid solution, ultrasonically treated 20min~60min obtains the P25 dispersion liquids with positive charge;To be prepared by Hummer ' s methods Graphene oxide the solution of 2mg/mL is configured to via ultrasonic wave added method;Clean quartz substrate is immersed in polyethyleneimine 30min~60min in amine aqueous solution, obtains the quartz substrate with positive charge;The quartz substrate with positive charge is soaked successively again Enter to graphene oxide solution and P25 dispersion liquids, dried up with deionized water rinsing after immersion is taken out every time and with nitrogen, born It is loaded with the quartz plate of one layer of graphene oxide/P25 laminated films;Above step is repeated, obtains being loaded with the THIN COMPOSITE that the number of plies is n The quartz plate of film;To be loaded with again under conditions of the quartz plate of the laminated film that the number of plies is n is 120 DEG C in temperature using hydrazine hydrate Reductase 12 h, is loaded with [Graphene/P25]nQuartz plate;
2nd, the quartz plate assembly array of black alkene/P25 multilayer films is loaded:Several are loaded with [Graphene/P25]nStone English piece is arranged in the reactor along fluid flow direction staggered parallel, and the left end of the reactor is provided with water inlet, and right-hand member sets Delivery port is equipped with, the water inlet and delivery port are diagonally positioned;
3rd, continuous photocatalytic degradation technique:Opening water pump makes pending solution circulate in the reactor, first in dark Under the conditions of circulate 20min~40min, then open uviol lamp, start light degradation process, every 30min to treating in reactor Degradation product carries out Concentration Testing, when after degradation product degraded is complete, i.e. completion fills Graphene/P25 laminated films based on secondary groups Continuous photocatalytic process;The pending solution is the rhodamine B solution that concentration is 10mg/L.
Operation principle:
The present invention connects layer electrostatic technique and is alternately assembled in its surface vertical direction with quartz plate as catalyst carrier, using layer Graphene oxide/P25 composite membranes, then reduction obtains load multilayer [Graphene/P25] under 120 DEG C of hydrazine hydrate effectsn(n generations Table alternately assembling the number of plies) quartz plate (one-level assembling), will load multilayer [Graphene/P25] quartz plate along flow direction row Into array (secondary groups dress).Dye solution is set continuously to flow through catalyst surface by pump.When ultraviolet light catalyst During surface, the electronics in P25 valence band is excited and transits to conduction band, is formed respectively with oxidation in valence band and conduction band and goes back proper energy The photohole and electronics of power.Due to the two-dimentional pi-conjugated structure of Graphene, electronics can be transferred to graphite by the conduction band of P25 Alkene.The electronics that these are captured by Graphene can react to form active oxygen species with dissolving oxygen in aqueous, further with Water reaction generation hydroxyl radical free radical (OH-), so that dye molecule is degraded.At the same time, the hole in valence band can be direct Oxidation dye molecule is so that dye molecule is degraded.The present invention prepares brand-new Graphene/P25 layers and connects layer using secondary groups dress technology Laminated film array, being combined again for electron-hole is effectively suppressed by introducing Graphene, so as to significantly improve the photocatalysis of P25 Degradation property.The structure novel catalysis material can conveniently realize efficiently separating for catalyst and degradation solution so that continuous light Degradation treatment technique substitutes current batch (-type) handling process research and is possibly realized;It is realized as organic dye solution industry rule Modelling continuous degradation basis prototype process.
Beneficial effects of the present invention:
1st, the novel photocatalysis membrane array of brand new is prepared using secondary groups dress technology, powder is used so as to avoid Later stage separating step during catalyst, using pump circulation fluid continuous degradation technology generations for the indirect stirring batch for generally using at present Secondary handling process, makes it possible the extensive continuous processing of waste water from dyestuff, is that the following real practical application of photocatalysis technology is established Fixed basis.
2nd, connect layer electrostatic technique using layer and alternately assemble Graphene/P25 composite membranes in its surface vertical direction, formed The heterogeneous energy-conservations of Graphene/P25 enough effectively suppress photo-generate electron-hole to being combined, so as to significantly improve the photocatalytic degradation of P25 Performance.Graphene is alternately assembled with P25 in addition, is effectively inhibited the reunion of P25 nano-particles, be conducive to light to urge Change performance to improve.The catalysis material for being obtained has that porosity is high, specific surface area is big, mechanical strength is big, photocatalysis performance is steady Calmly, the features such as long service life (repeatedly using performance unattenuated).High catalytic efficiency of the present invention, energy saving, low cost Honest and clean, module design, simple structure, it is easy to operation and maintenance.
Brief description of the drawings
Fig. 1 is the continuous photocatalytic mechanism figure that Graphene/P25 laminated films are filled based on secondary groups;
Fig. 2 is plural layers [Graphene/P25] prepared in embodiment one5SEM figure;
Fig. 3 is [Graphene/P25] prepared in embodiment one5(magnetic force is stirred laminated film under traditional batch mode Mix) contrasted with (pump circulation flowing) light degradation property under continuation mode of the present invention;
Fig. 4 is the performance comparison figure using embodiment one, embodiment three, example IV and the rhodamine B degradation of embodiment five; Wherein 1 is embodiment three, and 2 is example IV, and 3 is embodiment five, and 4 is embodiment one;As can be seen from the figure when load is compound When the number of plies of film is 5, laminated film has maximum photocatalysis efficiency.Therefore the laminated film that selection tool is of five storeys is used as rear The photochemical catalyst of continuous research.
Fig. 5 is the performance comparison figure of embodiment one, embodiment six and the photocatalytic degradation rhodamine B of embodiment seven;Wherein a is Rhodamine B degraded certainly under ultraviolet light during without catalyst, b is embodiment six, and c is embodiment seven, and d is embodiment one;
Fig. 6 is the comparison diagram that embodiment carries out dyestuff degraded for continuous 8 time.
Specific embodiment
Specific embodiment one:One kind of present embodiment is based on the continuous light that secondary groups fill Graphene/P25 laminated films What catalysis process was specifically carried out according to the following steps:
First, a layer Technical form Graphene/P25 multilayer films are connect using layer on quartz plate:P25 is dispersed in the salt that pH is 2 In acid solution, ultrasonically treated 20min~60min obtains the P25 dispersion liquids with positive charge;To be prepared by Hummer ' s methods Graphene oxide the solution of 2mg/mL is configured to via ultrasonic wave added method;Clean quartz substrate is immersed in polyethyleneimine 30min~60min in amine aqueous solution, obtains the quartz substrate with positive charge;The quartz substrate with positive charge is soaked successively again Enter to graphene oxide solution and P25 dispersion liquids, dried up with deionized water rinsing after immersion is taken out every time and with nitrogen, born It is loaded with the quartz plate of one layer of graphene oxide/P25 laminated films;Above step is repeated, obtains being loaded with the THIN COMPOSITE that the number of plies is n The quartz plate of film;To be loaded with again under conditions of the quartz plate of the laminated film that the number of plies is n is 120 DEG C in temperature using hydrazine hydrate Reductase 12 h, is loaded with [Graphene/P25]nQuartz plate;
2nd, the quartz plate assembly array of black alkene/P25 multilayer films is loaded:Several are loaded with [Graphene/P25]nStone English piece is arranged in the reactor along fluid flow direction staggered parallel, and the left end of the reactor is provided with water inlet, and right-hand member sets Delivery port is equipped with, the water inlet and delivery port are diagonally positioned;
3rd, continuous photocatalytic degradation technique:Opening water pump makes pending solution circulate in the reactor, first in dark Under the conditions of circulate 20min~40min, then open uviol lamp, start light degradation process, every 30min to treating in reactor Degradation product carries out Concentration Testing, when after degradation product degraded is complete, i.e. completion fills Graphene/P25 laminated films based on secondary groups Continuous photocatalytic process;The pending solution is the rhodamine B solution that concentration is 10mg/L.
Specific embodiment two:Present embodiment from unlike specific embodiment one:P25 dioxies described in step one The quality and pH of changing titanium are that the volume ratio of 2 hydrochloric acid solution is 1mg:2mL.Other steps and parameter and the phase of specific embodiment one Together.
Specific embodiment three:Present embodiment from unlike specific embodiment one or two:Described in step Above step is repeated, obtains being loaded with the quartz plate of the laminated film that the number of plies is 5.Other steps and parameter and specific embodiment One or three is identical.
Specific embodiment four:Unlike one of present embodiment and specific embodiment one to three:Institute in step 3 The power for stating uviol lamp is 300W.Other steps and parameter are identical with one of specific embodiment one to three.
Specific embodiment five:Unlike one of present embodiment and specific embodiment one to four:Controlled in step 3 The flow velocity of water pump processed is 8mL/s.Other steps and parameter are identical with one of specific embodiment one to four.
Specific embodiment six:A kind of continuous light based on secondary groups dress Graphene/P25 laminated films of present embodiment is urged The application of change is [rGO/P25] with Photocatalytic Degradation Property that will be prepared using LbL electrostatic assemblies technologynLaminated film is used In photocatalytic degradation rhodamine B under ultraviolet light, concrete operation method is as follows:[rGO/P25] that will be preparednThe parallel friendship of laminated film In quartz reactor for 10mg/L rhodamine B solution of the insertion equipped with 370mL, water pump is opened, rhodamine B is made under dark condition Solution circulation flow moves 30min;Open 300W uviol lamps and start Photocatalytic Degradation Process, UV-vis spectroscopy is used every 30min Photometer is detected to the concentration of the rhodamine B in reactor.
Beneficial effects of the present invention are verified by following examples:
Embodiment one:One kind of the present embodiment is based on the continuous photocatalysis method that secondary groups fill Graphene/P25 laminated films Specifically carry out according to the following steps:
First, one-level assembling:Quartz plate upper strata connects layer (LbL) Technical form Graphene/P25 multilayer films:By 3mg P25 dispersions In the hydrochloric acid solution that 6mL pH are 2, ultrasonically treated 20min~60min obtains the P25 dispersion liquids with positive charge;To pass through Graphene oxide prepared by Hummer ' s methods is configured to the solution of 2mg/mL via ultrasonic wave added method;By clean quartz substrate 30min~60min in polyethylenimine solution is immersed in, the quartz substrate with positive charge is obtained.Again by the quartz substrate point 10min and 15min in graphene oxide solution and P25 dispersion liquids is not immersed in, and with deionized water rinsing and nitrogen is used after taking-up Drying can obtain being loaded with the quartz plate of one layer of graphene oxide/P25 laminated films;Above step is repeated, is loaded with The number of plies is the quartz plate of 5 laminated film;The quartz plate that the laminated film that the number of plies is 5 will be loaded with again is 120 DEG C in temperature Under the conditions of use hydrazine hydrate reduction 2h, be loaded with [Graphene/P25]5Quartz plate;2nd, secondary groups dress:It is loaded with [stone Black alkene/P25]5Quartz plate assembly array:[Graphene/P25] is loaded by 55Quartz glass plate along fluid flow direction hand over Mistake is arranged in parallel in the reactor, and the left end of the reactor is provided with water inlet, and right-hand member is provided with delivery port, the water inlet It is diagonally positioned with delivery port;3rd, continuous photocatalytic degradation technique:Make pending solution recycle stream in the reactor using water pump Dynamic, flow velocity is 8mL/s, and 20min~40min is first circulated under dark condition, makes to treat degradation material in load [Graphene/P25]5 Quartz glass plate reach adsorption/desorption balance, then open 300W uviol lamps, start light degradation process, every 30min to anti- Degradation product carries out Concentration Testing to answer treating in device, when after degradation product degraded completely after, that is, complete based on secondary groups dress Graphene/ The continuous photocatalytic process of P25 laminated films;The pending solution is the rhodamine B solution that concentration is 10mg/L.
Embodiment two:The present embodiment is with the difference of embodiment one:When carrying out photocatalytic degradation reaction, using magnetic Power agitator is treated degradation material and is stirred, and rotating speed is 250rpm.Other are identical with embodiment one.
Embodiment three:The present embodiment is with the difference of embodiment one:The catalyst number of plies is 1 layer in step one, its He is identical with embodiment one.
Example IV:The present embodiment is with the difference of embodiment one:Repeated in step one 2 times, born It is loaded with the quartz glass plate of the laminated film that the number of plies is 3.Other are identical with embodiment one.
Embodiment five:The present embodiment is with the difference of embodiment one:Repeated in step one 6 times, born It is loaded with the quartz glass plate of the laminated film that the number of plies is 7.Other are identical with embodiment one.
Embodiment six:The present embodiment is with the difference of embodiment one:[oxygen is prepared using LbL electrostatic assembly technologies Graphite alkene/P25]5After laminated film, hydrazine hydrate reduction is not used, will directly load [graphene oxide/P25]5Quartz plate Photocatalytic degradation experiment is carried out in insertion quartz reactor.Other are identical with embodiment one.
Embodiment seven:The present embodiment is with the difference of embodiment one:Substituted using kayexalate solution Graphene oxide solution, is prepared [kayexalate/P25] using LbL electrostatic assembly technologies5Laminated film, uses preparation [kayexalate/P25]5Laminated film carries out photocatalytic degradation.Other are identical with embodiment one.
Fig. 1 is the continuous photocatalytic mechanism figure that Graphene/P25 laminated films are filled based on secondary groups;It will be seen from figure 1 that [GO/P25]nLaminated film is to connect a layer electrostatic technique by layer to be assembled on quartz supports substrate, followed by hydrazine hydrate also Former graphene oxide (GO) is finally loaded [rGO/P25] for reduced graphene (rGO)nThe thin quartz plate of MULTILAYER COMPOSITE.And And by the alternate intercalation reaction device of the quartz plate of obtained supported catalyst after, dye solution can be realized by pump circulation fluid Continuous light degradation process.
Fig. 2 is in embodiment one prepared [Graphene/P25]5The SEM figures of laminated film, can be from figure simultaneously To in the composite membrane presence of Graphene and P25, it was demonstrated that the successful preparation of multilayer film.And the porous knot of the surface porosity of film Structure, this is highly beneficial for photocatalytic degradation.
Fig. 3 is [Graphene/P25] prepared in embodiment one5(magnetic force is stirred laminated film under traditional batch mode Mix) contrasted with (pump circulation flowing) light degradation property under continuation mode of the present invention.It can be seen that being answered for prepared Close multilayer film catalyst [Graphene/P25]5For, continuous light degradation technique will be substantially due to traditional batch light degradation technique.
Fig. 4 is the performance comparison figure using embodiment one, embodiment three, example IV and the rhodamine B degradation of embodiment five; Wherein 1 is embodiment three, and 2 is example IV, and 3 is embodiment five, and 4 is embodiment one;As can be seen from the figure when load is compound When the number of plies of film is 5, laminated film has maximum photocatalysis efficiency.Therefore the laminated film that selection tool is of five storeys is used as rear The photochemical catalyst of continuous research.
Fig. 5 is the performance comparison figure of embodiment one, embodiment six and the photocatalytic degradation rhodamine B of embodiment seven;Wherein a is Rhodamine B degraded certainly under ultraviolet light during without catalyst, b is embodiment six, and c is embodiment seven, and d is embodiment one;Selection Rhodamine B is used as photodegradative target substance.For embodiment one, under 300W ultra violet lamps, with the increasing of light application time Plus, the concentration of dyestuff is constantly reduced, and rhodamine B can be made degradable after 180min, the color of dyestuff also from start piece Red becomes colorless.In order to further prove the degradation property of prepared embodiment one, and made under identical experiment condition For [graphene oxide/P25]5[kayexalate/P25]5Film as a comparison, wherein kayexalate pair Photocatalysis effect is without influence.When without catalyst, the degraded certainly of dyestuff can almost be ignored;And photocatalysis efficiency is according to [oxygen Graphite alkene/P25]5<[kayexalate/P25]5<[Graphene/P25]5Order gradually increase.Result above is proved Embodiment one has most excellent photocatalysis performance.
Fig. 6 is the comparison diagram that embodiment carries out dyestuff degraded for continuous 8 time;As can be seen from Figure 6 embodiment one is used After continuous 8 times carry out dyestuff degradation process, catalytic efficiency does not have obvious reduction, it was demonstrated that prepared catalyst has excellent Different stability, can be with Reusability.
Continuous photocatalytically degradating organic dye can effectively be realized by above example, catalyst has both certainly been solved and reclaimed difficult Problem, photocatalysis efficiency is improve again, can be used for high-volume sewage disposal.

Claims (5)

1. it is a kind of to be based on the continuous photocatalysis method that secondary groups fill Graphene/P25 laminated films, it is characterised in that based on secondary groups Fill what the continuous photocatalysis method of Graphene/P25 laminated films was specifically carried out according to the following steps:
First, a layer Technical form Graphene/P25 multilayer films are connect using layer on quartz plate:P25 is dispersed in the hydrochloric acid that pH is 2 molten In liquid, ultrasonically treated 20min~60min obtains the P25 dispersion liquids with positive charge;The oxygen that will be prepared by Hummer ' s methods Graphite alkene is configured to the solution of 2mg/mL via ultrasonic wave added method;Clean quartz substrate is immersed in polyethyleneimine molten 30min~60min in liquid, obtains the quartz substrate with positive charge;The quartz substrate with positive charge is immersed in successively again Graphene oxide solution and P25 dispersion liquids, dry up with deionized water rinsing after immersion is taken out every time and with nitrogen, are loaded with One layer of quartz plate of graphene oxide/P25 laminated films;Above step is repeated, it is the laminated film of n to obtain being loaded with the number of plies Quartz plate;To be loaded with again under conditions of the quartz plate of the laminated film that the number of plies is n is 120 DEG C in temperature using hydrazine hydrate reduction 2h, is loaded with [Graphene/P25]nQuartz plate;
2nd, the quartz plate assembly array of black alkene/P25 multilayer films is loaded:Several are loaded with [Graphene/P25]nQuartz plate Along the arrangement of fluid flow direction staggered parallel in the reactor, the left end of the reactor is provided with water inlet, and right-hand member is provided with Delivery port, the water inlet and delivery port are diagonally positioned;
3rd, continuous photocatalytic degradation technique:Opening water pump makes pending solution circulate in the reactor, first in dark condition Lower circulation 20min~40min, then opens uviol lamp, starts light degradation process, and treating in reactor is degraded every 30min Thing carries out Concentration Testing, when after degradation product degraded is complete, that is, completes the company based on secondary groups dress Graphene/P25 laminated films Continuous photocatalytic process;The pending solution is the rhodamine B solution that concentration is 10mg/L.
2. one kind according to claim 1 fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups, It is characterized in that the quality of P25 titanium dioxide described in step one is 1mg with the volume ratio of the hydrochloric acid solution that pH is 2:2mL.
3. one kind according to claim 1 fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups, It is characterized in that the repetition above step described in step one, obtains being loaded with the quartz plate of the laminated film that the number of plies is 5.
4. according to claim 3 a kind of based on the two multistage continuous photocatalysis sides for assembling Graphene/P25 laminated films Method, it is characterised in that the power of uviol lamp described in step 3 is 300W.
5. one kind according to claim 3 fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups, It is characterized in that the flow velocity that water pump is controlled in step 3 is 8mL/s.
CN201611206949.2A 2016-12-23 2016-12-23 One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups Pending CN106745481A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611206949.2A CN106745481A (en) 2016-12-23 2016-12-23 One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611206949.2A CN106745481A (en) 2016-12-23 2016-12-23 One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups

Publications (1)

Publication Number Publication Date
CN106745481A true CN106745481A (en) 2017-05-31

Family

ID=58920405

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611206949.2A Pending CN106745481A (en) 2016-12-23 2016-12-23 One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups

Country Status (1)

Country Link
CN (1) CN106745481A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108380213A (en) * 2018-03-19 2018-08-10 上海应用技术大学 It is a kind of can magnetic recovery graphene/optically catalytic TiO 2 composite material and preparation method
CN108636458A (en) * 2018-04-10 2018-10-12 沈阳环境科学研究院 A kind of thin web for dirty phenols in water pollutant light degradation catalysis
CN110182887A (en) * 2019-06-27 2019-08-30 中素新科技有限公司 The processing method of organic dyestuff in wastewater
CN112028401A (en) * 2020-08-27 2020-12-04 无锡阿尔美环保科技有限公司 Application of multilayer composite functional material in industrial circulating water quality stabilization treatment

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101474899A (en) * 2009-01-16 2009-07-08 南开大学 Grapheme-organic material layered assembling film and preparation method thereof
CN102380364A (en) * 2011-09-02 2012-03-21 武汉大学 Preparation method of TiO2/graphene composite film
KR20120079401A (en) * 2011-01-04 2012-07-12 이화여자대학교 산학협력단 Porous graphene-layered titanium oxide nanohybrids and production method thereof
CN102728337A (en) * 2012-06-08 2012-10-17 华北电力大学 Graphite / titanium dioxide composite material and preparation method thereof
CN102744068A (en) * 2012-07-20 2012-10-24 常州大学 Magnetic-separable titanium dioxide P25-ferrite-graphene nanometer catalyst and preparation method thereof
CN103936294A (en) * 2014-03-24 2014-07-23 同济大学 Preparation method of coated glass sheet and photocatalytic water purifying device

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101474899A (en) * 2009-01-16 2009-07-08 南开大学 Grapheme-organic material layered assembling film and preparation method thereof
KR20120079401A (en) * 2011-01-04 2012-07-12 이화여자대학교 산학협력단 Porous graphene-layered titanium oxide nanohybrids and production method thereof
CN102380364A (en) * 2011-09-02 2012-03-21 武汉大学 Preparation method of TiO2/graphene composite film
CN102728337A (en) * 2012-06-08 2012-10-17 华北电力大学 Graphite / titanium dioxide composite material and preparation method thereof
CN102744068A (en) * 2012-07-20 2012-10-24 常州大学 Magnetic-separable titanium dioxide P25-ferrite-graphene nanometer catalyst and preparation method thereof
CN103936294A (en) * 2014-03-24 2014-07-23 同济大学 Preparation method of coated glass sheet and photocatalytic water purifying device

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
YU-PENG ZHANG等: "Preparation of graphene and TiO2 layer by layer composite with highly photocatalytic efficiency", 《PROGRESS IN NATURAL SCIENCE: MATERIALS INTERNATIONAL》 *
叶志镇等: "《半导体薄膜技术与物理》", 30 September 2008, 浙江大学出版社 *
唐祝兴: "《新型磁性纳米材料的制备、修饰及应用》", 31 August 2016, 机械工业出版社 *
李春香: "层接层自组装改性TiO2薄膜的制备及光催化性能研究", 《中国博士学位论文全文数据库 工程科技Ⅰ辑》 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108380213A (en) * 2018-03-19 2018-08-10 上海应用技术大学 It is a kind of can magnetic recovery graphene/optically catalytic TiO 2 composite material and preparation method
CN108380213B (en) * 2018-03-19 2020-12-08 上海应用技术大学 Magnetically-recyclable graphene/titanium dioxide photocatalytic composite material and preparation method thereof
CN108636458A (en) * 2018-04-10 2018-10-12 沈阳环境科学研究院 A kind of thin web for dirty phenols in water pollutant light degradation catalysis
CN110182887A (en) * 2019-06-27 2019-08-30 中素新科技有限公司 The processing method of organic dyestuff in wastewater
CN112028401A (en) * 2020-08-27 2020-12-04 无锡阿尔美环保科技有限公司 Application of multilayer composite functional material in industrial circulating water quality stabilization treatment

Similar Documents

Publication Publication Date Title
CN106179262B (en) Composite material and preparation method and purposes with absorption-visible light photocatalytic degradation synergistic effect
CN105964256B (en) A kind of preparation method of hud typed ferroso-ferric oxide/graphene oxide composite nano catalyst
CN106745481A (en) One kind fills the continuous photocatalysis method of Graphene/P25 laminated films based on secondary groups
CN104909428B (en) A kind of Ag3PO4/TiO2The device and method of catalyst and low temperature plasma Combined Treatment bio-refractory organic wastewater
CN107159313A (en) A kind of core shell structure TiO2The preparation method of nanotube@Ti MOF catalyst
CN110252370A (en) A kind of two dimension ZnO/g-C3N4The Preparation method and use of composite photo-catalyst
CN107617447A (en) A kind of Ag@MOFs/TiO2The preparation method of photochemical catalyst and application
CN207153717U (en) A kind of optic catalytic composite material structure
CN106881111A (en) Composite bismuth vanadium photocatalyst of cuprous oxide and silver-colored mutual load and its preparation method and application
CN108640214A (en) One kind having photocatalysis performance seperation film and preparation method thereof
CN106694026A (en) Preparation method of core-shell type cuprous oxide photocatalyst
CN107029771A (en) Silver carbonate/silver/tungstic acid tri compound Z-type photochemical catalyst and its preparation method and application
CN107892354A (en) A kind of device and method of photocatalytic degradation of dye waste water
CN107199052A (en) A kind of silver-colored titanium dioxide metal-organic framework composite and its preparation method and application
Su et al. Heterostructured Bi2O2CO3/rGO/PDA photocatalysts with superior activity for organic pollutant degradation: Structural characterization, reaction mechanism and economic assessment
CN109529892A (en) A kind of nano strip MOA composite photo-catalyst preparation method
CN104368338B (en) A kind of have amido modified Pd/TiO2The preparation method of photocatalyst
CN108435149A (en) A kind of nano cuprous oxide radical dye sorbing material and preparation method thereof
CN106732650B (en) A kind of and doping and load dual modified perovskite type photocatalyst and preparation method thereof
CN108554458A (en) Core/membranous type composite bismuth vanadium photocatalyst and preparation method thereof
Liu et al. The advanced development of floatable photocatalysts: Preparation, advantages, and application
CN107055678A (en) A kind of triphase catalytic oxidation sewage water treatment method and reactor
CN109201091A (en) A kind of purification of water quality magnetic response type nucleocapsid photochemical catalyst and preparation method thereof
CN107955523B (en) A kind of environmental-protecting self visible light catalytic coating and its preparation and application
CN108906015A (en) A kind of nano-onions carbon/composite titania/silica photocatalyst material and its preparation method and application

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
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20170531