CN108993548A - A kind of visible light responsive photocatalyst and application thereof, preparation method and application method - Google Patents

A kind of visible light responsive photocatalyst and application thereof, preparation method and application method Download PDF

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CN108993548A
CN108993548A CN201810797202.1A CN201810797202A CN108993548A CN 108993548 A CN108993548 A CN 108993548A CN 201810797202 A CN201810797202 A CN 201810797202A CN 108993548 A CN108993548 A CN 108993548A
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solution
bismuth
catalyst
visible light
organic matter
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董晓丽
华承贺
王宇
郑楠
马红超
张秀芳
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Dalian Polytechnic University
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Dalian Polytechnic University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/06Halogens; Compounds thereof
    • B01J35/39
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/10Heat treatment in the presence of water, e.g. steam
    • 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
    • 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
    • C02F2101/34Organic compounds containing oxygen
    • 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
    • C02F2101/36Organic compounds containing halogen
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

Abstract

The invention discloses a kind of visible light-responded photochemical catalysts, to hydrogenate bismuth deposit bismuth oxybromide, molecular formula H-Bi BiOBr, for the organic matter in Photocatalytic Activity for Degradation water body.The preparation method of catalyst, comprising steps of 1, take Organic Alcohol as solvent;2, organic alcohol solvent is added in bismuth salt compound and bromide compound, mixes and is sufficiently stirred;3, neutral solution is added after stirring to clarify solution and a certain amount of reducing agent is added, is fitted into reaction kettle after stirring, carries out isothermal reaction;4, it is cooled to room temperature and is centrifuged and is repeatedly washed with water and ethanol solution, collect powder after dry;5, it calcines under an atmosphere of hydrogen, obtains hydrogenation bismuth deposit bismuth oxybromide.The hydrogenation bismuth deposit bismuth oxybromide photocatalyst that the method for the present invention obtains is environmentally friendly, material source is extensive, cheap, method is controllable and easy to operate, can be produced in batches, the photocatalysis performance with good degradation of organic substances.

Description

A kind of visible light responsive photocatalyst and application thereof, preparation method and application method
Technical field
The present invention relates to catalysis material technical fields, more specifically to a kind of hydrogenation bismuth deposit bismuth oxybromide (H- Bi@BiOBr) visible light-responded organic matter degradation photochemical catalyst preparation and application.
Background technique
It is well known that the organic matter especially dyestuff and antibiotic pollutant in water body seriously affect Water quality, destroy Environment threatens human health.Although traditional biological treatment can handle Organic substance in water well, due to microorganism Specificity, to increase processing cost.In addition to this, biological treatment process is longer, safeguards more difficult.Compared to biological treatment Method, photocatalysis oxidation technique are thoroughly received significant attention because of its environment-protection low-consumption, processing.But due to semiconductor catalyst quantum Low efficiency, recycling rate of waterused is limited and is difficult to the problems such as recycling and is difficult to meet actual needs.For semiconductor light-catalyst, by In biggish forbidden bandwidth make it low to the utilization rate of sunlight and its practical application in another huge challenge.
Now, more and more photochemical catalysts are used in photocatalysis degradation organic contaminant.Such as: titanium dioxide, two Molybdenum sulfide, graphite phase carbon nitride, bismuth tungstate, pucherite etc..However, since bismuth oxybromide (BiOBr) has unique stratiform knot Structure is conducive to electron-transport, and suitable forbidden bandwidth has wider light abstraction width, and has simple production process, cheap, nothing The advantages that malicious.Nevertheless, traditional BiOBr still shows lower organic matter degradation ability.
Summary of the invention
It is an object of that present invention to provide a kind of visible light-responded organic matter degradation photochemical catalyst and its synthetic method, purposes and Biodegrading process.
To achieve the goals above, the technical solution of the present invention is as follows:
A kind of visible light-responded organic matter degradation photochemical catalyst of the present invention, catalyst are hydrogenation bismuth deposit bismuth oxybromide, point Minor H-Bi@BiOBr.Structure is the flower ball-shaped microballoon with bismuth simple substance and Lacking oxygen.
Catalyst provided by the invention, for the dyestuff or antibiotic organic matter under visible light in catalytic degradation water body.Institute Stating dyestuff is anthraquinone dyes or azo dyes, and the antibiotic is Ofloxacin, terramycin, cephalosporin or penicillin. Wherein anthraquinone dyes are reactive brilliant blue, reactive brilliant red, Disperse Blue 2BLN, RSN vat blue, the gorgeous orchid RAW, rhodamine B of faintly acid It is methyl orange, methylene blue, tonyred etc. Deng, azo dyes.
The present invention provides a kind of preparation methods of visible light-responded degradation of organic substances photochemical catalyst, include the following steps:
S1, at room temperature using ethylene glycol, diethylene glycol, triethylene glycol, isopropanol or glycerine as solvent;
S2, the alcoholic solvent is added in bismuth salt compound and bromide compound, mixes and is sufficiently stirred;The bismuth salt chemical combination Object is five nitric hydrate bismuths, bismuth sulfate or bismuth ion complex compound;The bromide compound is sodium bromide, potassium bromide, CTAB or 2- Ethylamine hydrobromide;
S3, it stirs to clarify and neutral solution is added after solution stirs 20~80min, add reducing agent solution, stirring 3~ It is fitted into after 10min in the autoclave that pressure is 1~2Mpa, carries out 120~180 DEG C of isothermal reactions;
S4, it is cooled to room temperature and is centrifuged and is washed with water and ethanol solution, collect powder after dry at 50~80 DEG C End;
S5,2~6h is calcined under 100~300 DEG C, 320~380mL/min atmosphere of hydrogen, obtain hydrogenation bismuth deposit bromine oxygen Change bismuth.
Wherein, in step s3, the neutral solution is the monohydric alcohols such as methanol, ethyl alcohol, isopropanol, the tert-butyl alcohol, octanol;Institute Stating reducing agent solution is hydrazine hydrate, thiocarbamide, sodium citrate, ascorbic acid or sodium borohydride solution.
The present invention provides a kind of preparation methods of visible light-responded organic matter degradation photochemical catalyst, specifically include following step It is rapid:
S1, at room temperature using 20~40ml ethylene glycol, diethylene glycol, triethylene glycol, isopropanol or glycerine as solvent;
S2, the alcoholic solvent is added in 0.1~0.5g bismuth salt compound and 0.01~0.3g bromide compound, mixes and fills Divide stirring 5~30min;
S3,40~80mL neutral solution, 20~80min of stirring is added after stirring to clarify solution, adds 0.1~4mL also Former agent solution stirs 3~10min, is packed into autoclave after acquired solution stirring, carry out 120~180 DEG C of isothermal reaction 10h with On;
S4, it is cooled to room temperature and is centrifuged and is washed 4~8 times with water and ethanol solution, after 50~80 DEG C dry, receive Collect powder;
S5,2~6h is calcined under 100~300 DEG C, 320~380mL/min atmosphere of hydrogen, obtain hydrogenation bismuth deposit bromine oxygen Change bismuth.
Wherein, when isothermal reaction described in step S3, it is 60% that the volume for filling solution, which accounts for the ratio of autoclave liner volume, ~90%, the reaction time be 10~for 24 hours.
The present invention provides a kind of using the method for dyestuff or antibiotic in above-mentioned catalyst degradation water, including following Step: photochemical catalyst H-Bi@BiOBr being added into dyestuff or antibiotic organic solution, and maintains room temperature, is carrying out photocatalysis Before, no light stirs 30min, then filters out catalyst after stirring 40~150min under visible light photograph.
Content of organics is 5~50mg/L in organic solution in above-mentioned reaction, the additional amount of catalyst meets 5~ 30mg.The dyestuff be anthraquinone dyes or azo dyes, the antibiotic be Ofloxacin, terramycin, cephalosporin or Penicillin.Wherein anthraquinone dyes be reactive brilliant blue, reactive brilliant red, Disperse Blue 2BLN, RSN vat blue, the gorgeous orchid RAW of faintly acid, Rhodamine B etc., azo dyes are methyl orange, methylene blue, tonyred etc..
The present invention has the advantage that
Photochemical catalyst of the invention is H-Bi@BiOBr, and not only there is photochemical catalyst of the invention good visible light light to urge Change degradation of organic substances performance, and possesses higher quantum efficiency.Under visible light, H-Bi@BiOBr can be incited somebody to action within a hour Concentration is that the rhodamine B of 10mg/L is degradable, and degradation efficiency is 1.2 times of Bi@BiOBr, is 2.5 times of traditional BiOBr. Not only there is significant organic matter degradation effect, quantum efficiency also with higher under visible light.In Environmental pollution and control Field has broad application prospects, and strong theoretical basis is provided for the type catalyst.
Detailed description of the invention
Fig. 1 is the XRD diffraction pattern of 1 catalyst of embodiment.
Fig. 2 is the scanning electron microscope (SEM) photograph of 1 catalyst of embodiment.
Fig. 3 is the UV-vis abosrption spectrogram of 1 catalyst of embodiment.
Fig. 4 is that the forbidden bandwidth of 1 catalyst of embodiment estimates spectrogram.
Fig. 5 is the current versus time curve figure of 1 catalyst of embodiment.
Fig. 6 is the AC impedance figure of 1 catalyst of embodiment.
Fig. 7 is the photocatalytic degradation of dye organic matter effect picture of 4~7 catalyst of embodiment.
Fig. 8 is the photocatalytic degradation of dye organic matter effect picture of Examples 1 to 4,7 catalyst.
Fig. 9 is the photocatalytic degradation antibiotic organic matter effect picture of 4~7 catalyst of embodiment.
Figure 10 is the photocatalytic degradation antibiotic organic matter effect picture of Examples 1 to 4,7 catalyst.
Specific embodiment
The present invention it is a kind of hydrogenation bismuth deposit bismuth oxybromide efficient visible light response organic matter degradation photochemical catalyst preparation and Application method belongs to catalysis material technical field.This method comprises the following steps: bismuth salt and bromide are dissolved in alcoholic solution In;Neutral solution is added and reducing agent solution is added;Carry out hydro-thermal reaction;With water and ethanol washing and it is centrifugated;It is dry After obtain solid powder;Hydrogen calcining is passed through in tube furnace;It is cooled to room temperature and obtains product.To dyestuff or antibiotic organic matter Above-mentioned catalyst is added in solution, no light stirs evenly, then stirs under visible light photograph, and catalyst is filtered out after the completion of degradation. The hydrogenation bismuth deposit bismuth oxybromide photocatalyst that the method for the present invention obtains is environmentally friendly, material source is extensive, cheap, method It is controllable and easy to operate, can be produced in batches, have good Visible Light Induced Photocatalytic organic matter photocatalysis performance.
Below with reference to the attached drawing in the embodiment of the present invention, come technical solution in the embodiment of the present invention make it is clear, Complete statement.Embodiments described below is only a part of the invention, is not whole embodiments.This field Technical staff's above content according to the present invention is made some nonessential improvement and is all belonged to the scope of protection of the present invention.
It is an object of the present invention to provide a kind of visible light-responded organic matter degradation photochemical catalysts, provide described in a kind of prepare The method of photochemical catalyst, while a kind of biodegrading process of visible light-responded organic matter degradation photochemical catalyst being provided.
Using 20~40mL ethylene glycol, diethylene glycol, triethylene glycol, isopropanol or glycerine as solvent, room in the present invention It is reacted under temperature.The alcohol includes but is not limited to ethylene glycol, diethylene glycol, triethylene glycol, isopropanol or glycerine.
The alcoholic solution is added in 0.1~0.5g bismuth salt compound and 0.01~0.3g bromide compound, is mixed and abundant Stirring, mixing time are 5~30min.The bismuth-containing compound includes but is not limited to five nitric hydrate bismuths, bismuth sulfate or bismuth ion Complex compound;The bromine-containing compound includes but is not limited to sodium bromide, potassium bromide, CTAB or 2- ethylamine hydrobromide.
40~80mL neutral solution is added after above-mentioned solution is stirred to clarify solution in the present invention, and 0.1~4mL is added Reducing solution, acquired solution are packed into autoclave after stirring 3~10min, carry out 120~180 DEG C of isothermal reactions 10~ 24h.The neutral solution includes but is not limited to the monohydric alcohols such as methanol, ethyl alcohol, isopropanol, the tert-butyl alcohol or octanol.The reproducibility Solution is hydrazine hydrate, thiocarbamide, sodium citrate, ascorbic acid or sodium borohydride solution.Product, which is cooled to room temperature, to be centrifuged And washed 4 times~8 times with water and ethanol solution, powder is collected after dry at 50~80 DEG C.Wherein, when synthetic reaction, solution is filled Volume account for autoclave liner volume ratio be 60%~90%;Reaction time be 10~for 24 hours.
2~6h is calcined under 100~300 DEG C, 320~380mL/min atmosphere of hydrogen, obtains final products H-Bi@ BiOBr。
The above-mentioned photochemical catalyst of 5~30mg is added in the present invention into 5~50mg/L dyestuff or antibiotic organic solution, and Room temperature is maintained, before carrying out photocatalysis, no light stirs 30min, then filters out and urge after 40~150min of stirring under visible light photograph Agent.
Compared with existing photocatalysis technology, the present invention is had the advantage that
(1) the H-Bi@BiOBr catalysis material that the present invention obtains not only there is good Photocatalytic Activity for Degradation to have Machine physical performance, and possess higher quantum efficiency.Under visible light, sieve that can be 10mg/L by concentration within a hour Red bright B is degradable, and degradation efficiency is 1.2 times of Bi@BiOBr, is 2.5 times of traditional BiOBr.Have under visible light aobvious The organic matter degradation effect of work.It has broad application prospects in Environmental pollution and control field.
(2) preparation method of H-Bi@BiOBr catalysis material is environmentally protective, easy to operate, cheap, sets to special Low for requiring, controllability is strong, has certain practicability.
Embodiment 1
Five nitric hydrate bismuth of 0.24g and 0.102g sodium bromide are added in 10mL ethylene glycol solution, 20min is sufficiently stirred 25mL aqueous isopropanol is added after to clear solution, 1mL thiourea solution is added after stirring 30min in mixed solution, after stirring 5min It is packed into 1~2Mpa autoclave, carries out 160 DEG C of incubation water heating reaction 12h.Product is cooled to room temperature to be centrifuged and be used in combination Water and ethanol solution are washed 6 times, collect powder after dry in 60 DEG C.4h is calcined under 200 DEG C, 360mL/min atmosphere of hydrogen, is obtained Final products H-Bi@BiOBr.
Fig. 1 is the H-Bi@BiOBr photochemical catalyst XRD diffracting spectrum that the present embodiment obtains, through comparing with PDF standard card It learns, the BiOBr obtained for tetragonal phase.
Fig. 2 is the H-Bi@BiOBr photochemical catalyst scanning electron microscope (SEM) photograph that the present embodiment obtains, and being obtained is what piece was polymerized Diameter is about 1.5 μm of bouquets.
Fig. 3 is the H-Bi@BiOBr photochemical catalyst UV-vis absorption spectrum that the present embodiment obtains, and is inhaled compared to pure phase BiOBr Side red shift is received, is obviously improved in visible-range internal absorbance, there is stronger light abstraction width.
Fig. 4 is the forbidden bandwidth estimation map for the H-Bi@BiOBr photochemical catalyst that the present embodiment obtains, the band of resulting materials Gap relative narrower accelerates electron-transport speed, to promote photocatalytic activity.
Fig. 5 is the H-Bi@BiOBr photochemical catalyst photocurrent-time curve figure that the present embodiment obtains, compared to pure phase BiOBr presents stronger photoelectric current, illustrates to have efficiently separated light induced electron and hole.
Fig. 6 is that the H-Bi@BiOBr photochemical catalyst AC impedance figure that the present embodiment obtains shows compared to pure phase BiOBr Lesser resistance, at the same illustrate it is for the recombination rate of photo-generated carrier low, it is preferable to promote charge conversion and efficiently separate.
Embodiment 2
Five nitric hydrate bismuth of 0.24g and 0.102g sodium bromide are added in 10mL ethylene glycol solution, 20min is sufficiently stirred 25mL aqueous isopropanol is added after to clear solution, mixed solution stirs the thiourea solution of addition 1mL after 30min, stirs 5min It is packed into 1~2Mpa autoclave afterwards, carries out 160 DEG C of incubation water heating reaction 12h.Product, which is cooled to room temperature, to be centrifuged simultaneously It is washed 6 times with water and ethanol solution, collects powder after dry in 60 DEG C.4h is calcined under 250 DEG C, 360mL/min atmosphere of hydrogen, is obtained To final products H-Bi@BiOBr.
Embodiment 3
Five nitric hydrate bismuth of 0.24g and 0.102g sodium bromide are added in 10mL ethylene glycol solution, 20min is sufficiently stirred 25mL aqueous isopropanol is added after to clear solution, mixed solution stirs the thiourea solution of addition 1mL after 30min, stirs 5min It is packed into 1~2Mpa autoclave afterwards, carries out 160 DEG C of incubation water heating reaction 12h.Product, which is cooled to room temperature, to be centrifuged simultaneously It is washed 6 times with water and ethanol solution, collects powder after dry in 60 DEG C.4h is calcined under 150 DEG C, 360mL/min atmosphere of hydrogen, is obtained To final products H-Bi@BiOBr.
Embodiment 4
Five nitric hydrate bismuth of 0.24g and 0.102g sodium bromide are added in 10mL ethylene glycol solution, 20min is sufficiently stirred 25mL aqueous isopropanol is added after to clear solution, mixed solution is added 1.0mL thiourea solution after stirring 30min, stirs 5min It is packed into 1~2Mpa autoclave afterwards, carries out 160 DEG C of incubation water heating reaction 12h.Product, which is cooled to room temperature, to be centrifuged simultaneously It is washed 6 times with water and ethanol solution, collects powder after dry in 60 DEG C.Obtain final products Bi@BiOBr.
Embodiment 5
Five nitric hydrate bismuth of 0.24g and 0.102g sodium bromide are added in 10mL ethylene glycol solution, 20min is sufficiently stirred 25mL aqueous isopropanol is added after to clear solution, mixed solution is added 0.5mL thiourea solution after stirring 30min, stirs 5min It is packed into 1~2Mpa autoclave afterwards, carries out 160 DEG C of incubation water heating reaction 12h.Product, which is cooled to room temperature, to be centrifuged simultaneously It is washed 6 times with water and ethanol solution, collects powder after dry in 60 DEG C.Obtain final products Bi@BiOBr.
Embodiment 6
Five nitric hydrate bismuth of 0.24g and 0.102g sodium bromide are added in 10mL ethylene glycol solution, 20min is sufficiently stirred 25mL aqueous isopropanol is added after to clear solution, 2mL thiourea solution is added after stirring 30min in mixed solution, after stirring 5min It is packed into 1~2Mpa autoclave, carries out 160 DEG C of incubation water heating reaction 12h.Product is cooled to room temperature to be centrifuged and be used in combination Water and ethanol solution are washed 6 times, collect powder after dry in 60 DEG C.Obtain final products Bi@BiOBr.
Embodiment 7
Five nitric hydrate bismuth of 0.24g and 0.102g sodium bromide are added in 10mL ethylene glycol solution, 20min is sufficiently stirred 25mL aqueous isopropanol is added after to clear solution, mixed solution is packed into 1~2Mpa autoclave after stirring 30min, carries out 160 DEG C of incubation water heatings react 12h.Product, which is cooled to room temperature, to be centrifuged and is washed 6 times with water and ethanol solution, dry in 60 DEG C Powder is collected after dry.Obtain final products BiOBr.
The test of photocatalysis dyestuff organic matter degradation is carried out for Examples 1 to 7 sample.
All photocatalysis experiments are at room temperature that visible light executes with 300W xenon lamp band 420nm cut out tab.Light is urged Change degradation of dye organic matter process: the rhodamine B solution of 0.01g catalyst and 50mL being added in glass photocatalytic reactor (solution concentration 10mg/L), and recirculated water is passed through to maintain room temperature.Before carrying out photocatalysis, no light stirring 30min, then Visible light extracts 4ml solution out according to lower every 10min or 20min.It is further filtered with 0.22 μm of filter, and in ultraviolet specrophotometer Absorbance is measured under specific absorption wavelength, for indicating palliating degradation degree.Photocatalysis rhodamine B is carried out for Examples 1 to 7 sample Organic matter degradation test.
Fig. 7 illustrates 2 hours photocatalytic degradation of dye organic matter effects of 4~7 catalyst of embodiment.It is obvious that implementing 4 catalyst of example shows optimal photocatalytic degradation of organic matter effect, and the degradation rate of rhodamine B reaches 98.2% after 2 hours.It is real Applying 5 catalyst of example is 93.0%, and 6 catalyst of embodiment is 95.5%, and 7 catalyst of untreated embodiment is 52.2%. Fig. 8 illustrates Examples 1 to 4,1 hour photocatalytic degradation of organic matter effect of 7 catalyst.It is obvious that 1 catalyst of embodiment is aobvious Optimal photocatalytic degradation of organic matter effect is shown, the degradation rate of rhodamine B reaches 99.5% after 1 hour.2 catalyst of embodiment It is 96.5%, 3 catalyst of embodiment is 89.6%, and 4 catalyst of embodiment is 80.5%, and untreated embodiment 7 is catalyzed Agent is 29.2%.To find out, H-Bi@BiOBr photochemical catalyst of the invention possesses brilliant photocatalytic degradation of organic matter effect.
The test of photocatalysis antibiotic organic matter degradation is carried out for Examples 1 to 7 sample.
All photocatalysis experiments are at room temperature that visible light executes with 300W xenon lamp band 420nm cut out tab.Light is urged Change degradation antibiotic organic matter process: 0.01g catalyst being added in glass photocatalytic reactor and the Ofloxacin of 50mL is molten Liquid (solution concentration 10mg/L), and recirculated water is passed through to maintain room temperature.Before carrying out photocatalysis, no light stirs 30min, then Every 30min extracts 4ml solution out under visible light photograph.It is further filtered with 0.22 μm of filter, and specific in ultraviolet specrophotometer Absorbance is measured under absorbing wavelength, for indicating palliating degradation degree.Carrying out photocatalytic-oxidation Flucloxacillin for Examples 1 to 7 sample has The degradation test of machine object.
Fig. 9 illustrates 4 hours photocatalytic degradation antibiotic organic matter effects of 4~7 catalyst of embodiment.It is obvious that real It applies 4 catalyst of example and shows optimal photocatalytic degradation of organic matter effect, the degradation rate of Ofloxacin reaches after 4 hours 77.5%.5 catalyst of embodiment is 61.4%, and 6 catalyst of embodiment is 71.2%, and 7 catalyst of untreated embodiment It is 32.2%.Figure 10 illustrates Examples 1 to 4,3 hours photocatalytic degradation of organic matter effects of 7 catalyst.It is obvious that implementing 1 catalyst of example shows optimal photocatalytic degradation of organic matter effect, and the degradation rate of Ofloxacin reaches 81.9% after 3 hours. 2 catalyst of embodiment is 76.9%, and 3 catalyst of embodiment is 71.9%, and 4 catalyst of embodiment is 64.8%, and unprocessed 7 catalyst of embodiment be 25.3%.To find out, H-Bi@BiOBr photochemical catalyst of the invention possesses brilliant photocatalysis drop Solve organic matter effect.
Catalyst provided by the invention, for the dyestuff or antibiotic organic matter under visible light in catalytic degradation water body.Needle To different dyes and antibiotic, there are different degradation effects;It is prominent for anthraquinone dyes or azo dyes effect.Particular for Anthraquinone dyes or the first such as gorgeous orchid RAW, the rhodamine B of reactive brilliant blue, reactive brilliant red, Disperse Blue 2BLN, RSN vat blue, faintly acid The antibiosis such as azo dyes or Ofloxacin, terramycin, cephalosporin, penicillin such as base orange, methylene blue, tonyred are known as aobvious The organic matter degradation effect of work.Since length is limited, whole organic matters and its test data can not be enumerated, the present invention only offer portion Separating tests data support beneficial effects of the present invention.And the present invention can not also enumerate the specific organic matter for all having degradation effect, It will be appreciated by those skilled in the art that, protection scope of the present invention should include all catalyst of the present invention according to claim There is the organic matter of degradation effect;And the dyestuff or antibiotic for utilizing catalyst degradation of the present invention invalid, it is not protected in the present invention In range, inventor does not determine specifically dyestuff or antibiotic without degradation effect at present.
In order to preferably carry out organic matter degradation light-catalyzed reaction using BiOBr, present invention employs bismuth deposits and low temperature The method of hydrogen calcining, is successfully prepared the BiOBr microballoon of the flower ball-shaped with bismuth with elementary and a large amount of Lacking oxygens.For dyestuff and The performance of good photocatalytic degradation of organic matter is presented in antibiotic organic wastewater, catalyst.Due to the deposition of bismuth simple substance, at it While carrying out transmitting electronic action, SPR effect can more absorb visible light, enhance visible light utilization efficiency.Due to hydrogen The reducing property of gas, hydrogenation process can make nano grain surface confusion to remove oxygen atom.This is that a kind of easy method is gone Manufacture Lacking oxygen and the amount for controlling Lacking oxygen.Meanwhile 3D micro-sphere structure possesses a high specific surface area, this material presents Zhuo Adsorption capacity more, so that under visible light, there is good organic matter degradation effect.
The foregoing is only a preferred embodiment of the present invention, but scope of protection of the present invention is not limited thereto, Anyone skilled in the art within the technical scope of the present disclosure, according to the technique and scheme of the present invention and its Inventive concept is subject to equivalent substitution or change, should be covered by the protection scope of the present invention.

Claims (14)

1. a kind of visible light-responded organic matter degradation photochemical catalyst, which is characterized in that catalyst is hydrogenation bismuth deposit bismuth oxybromide, Molecular formula is H-Bi@BiOBr.
2. photochemical catalyst according to claim 1, which is characterized in that in the flower ball-shaped microballoon knot with bismuth simple substance and Lacking oxygen Structure.
3. a kind of purposes of catalyst, which is characterized in that for the dyestuff or antibiotic organic matter in water body of degrading under visible light.
4. the purposes of catalyst according to claim 3, which is characterized in that the dyestuff is that anthraquinone dyes or azo contaminate Material, the antibiotic are Ofloxacin, terramycin, cephalosporin or penicillin.
5. the purposes of catalyst according to claim 4, which is characterized in that the anthraquinone dyes are reactive brilliant blue, activity The gorgeous orchid RAW of bright red, Disperse Blue 2BLN, RSN vat blue, faintly acid or rhodamine B, the azo dyes are methyl orange, methylene Base indigo plant or tonyred.
6. a kind of preparation method of visible light-responded organic matter degradation photochemical catalyst, which comprises the steps of:
S1, at room temperature using ethylene glycol, diethylene glycol, triethylene glycol, isopropanol or glycerine as solvent;
S2, the alcoholic solvent is added in bismuth salt compound and bromide compound, mixes and is sufficiently stirred;The bismuth salt compound is Five nitric hydrate bismuths, bismuth sulfate or bismuth ion complex compound;The bromide compound is sodium bromide, potassium bromide, CTAB or 2- ethamine Hydrobromate;
S3, it stirs to clarify and neutral solution is added after solution stirs 20~80min, add reducing agent solution, stirring 3~ It is fitted into after 10min in the autoclave that pressure is 1~2Mpa, carries out 120~180 DEG C of isothermal reactions;
S4, it is cooled to room temperature and is centrifuged and is washed with water and ethanol solution, collect powder after dry at 50~80 DEG C;
S5,2~6h is calcined under 100~300 DEG C, 320~380mL/min atmosphere of hydrogen, obtain hydrogenation bismuth deposit bismuth oxybromide.
7. the preparation method of visible light-responded organic matter degradation photochemical catalyst according to claim 6, which is characterized in that step In S3, the neutral solution is methanol, ethyl alcohol, isopropanol, the tert-butyl alcohol or octanol.
8. the preparation method of visible light-responded organic matter degradation photochemical catalyst according to claim 6, which is characterized in that step In S3, the reducing agent solution is hydrazine hydrate, thiocarbamide, sodium citrate, ascorbic acid or sodium borohydride solution.
9. according to the preparation method of any visible light-responded organic matter degradation photochemical catalyst of claim 6~8, feature exists In, comprising the following steps:
S1, at room temperature using 20~40ml ethylene glycol, diethylene glycol, triethylene glycol, isopropanol or glycerine as solvent;
S2, the alcoholic solvent is added in 0.1~0.5g bismuth salt compound and 0.01~0.3g bromide compound, mixes and sufficiently stirs Mix 5~30min;
S3,40~80mL neutral solution, 20~80min of stirring is added after stirring to clarify solution, adds 0.1~4mL reducing agent Solution stirs 3~10min, is packed into autoclave after acquired solution stirring, carries out 120~180 DEG C of isothermal reaction 10h or more;
S4, it is cooled to room temperature and is centrifuged and is washed 4~8 times with water and ethanol solution, after 50~80 DEG C dry, collect powder End;
S5,2~6h is calcined under 100~300 DEG C, 320~380mL/min atmosphere of hydrogen, obtain hydrogenation bismuth deposit bismuth oxybromide.
10. the preparation method of visible light-responded organic matter degradation photochemical catalyst according to claim 9, which is characterized in that step When isothermal reaction described in rapid S3, it is 60%~90% that the volume for filling solution, which accounts for the ratio of autoclave liner volume, the reaction time For 10~for 24 hours.
11. a kind of use the method for dyestuff or antibiotic in above-mentioned catalyst degradation water, which is characterized in that dyestuff or resist Photochemical catalyst H-Bi BiOBr is added in raw element organic solution, and maintains room temperature, before carrying out photocatalysis, stirs 30min, then Catalyst is filtered out after stirring 40~150min under visible light photograph.
12. the method for dyestuff or antibiotic in water of degrading according to claim 11, which is characterized in that have in organic solution Machine object content is 5~50mg/L, and the additional amount of catalyst meets 5~30mg.
13. the method for dyestuff or antibiotic in water of degrading according to claim 11, which is characterized in that the dyestuff is anthraquinone Class dyestuff or azo dyes, the antibiotic are Ofloxacin, terramycin, cephalosporin or penicillin.
14. the method for dyestuff or antibiotic in the 3 degradation water according to claim 1, which is characterized in that the anthraquinone dyes For reactive brilliant blue, reactive brilliant red, Disperse Blue 2BLN, RSN vat blue, the gorgeous orchid RAW of faintly acid or rhodamine B, the azo dye Material is methyl orange, methylene blue or tonyred.
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