CN106166483B - A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation method and application - Google Patents

A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation method and application Download PDF

Info

Publication number
CN106166483B
CN106166483B CN201610582809.9A CN201610582809A CN106166483B CN 106166483 B CN106166483 B CN 106166483B CN 201610582809 A CN201610582809 A CN 201610582809A CN 106166483 B CN106166483 B CN 106166483B
Authority
CN
China
Prior art keywords
tio
graphene
hybrid material
graphene oxide
mycotoxin
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201610582809.9A
Other languages
Chinese (zh)
Other versions
CN106166483A (en
Inventor
白小娟
孙长坡
罗晓宏
伍松陵
王峻
柴成梁
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.)
Academy of Sciences, State Bureau of Food and Materials Reserve
Original Assignee
Academy of State Administration of Grain
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 Academy of State Administration of Grain filed Critical Academy of State Administration of Grain
Priority to CN201610582809.9A priority Critical patent/CN106166483B/en
Publication of CN106166483A publication Critical patent/CN106166483A/en
Application granted granted Critical
Publication of CN106166483B publication Critical patent/CN106166483B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/06Silicon, titanium, zirconium or hafnium; Oxides or hydroxides thereof
    • B01J21/063Titanium; Oxides or hydroxides thereof
    • B01J35/39

Abstract

The invention discloses a kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2, hybrid material graphene/TiO2It mainly include TiO2Nano particle and its surface coated single-layer or multi-layer graphene film, it is by graphene oxide and TiO2Nano particle is according to the ratio that mass ratio is 0.1-10:100 by made from hydrothermal synthesis method;In addition, the present invention has investigated hybrid material graphene/TiO by the conditions such as graphene modified amount and light degradation time2Influence to photocatalytic degradation mycotoxin.The present invention has the hybrid material graphene/TiO of high activity by hydro-thermal method preparation2, simple process is suitable for industrial mass production, and Photocatalyst is applied to degradative fungi toxin field has very high application prospect and practical value.

Description

A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation Methods and applications
Technical field
The invention belongs to analytical chemistry fields, and in particular to a kind of hybrid material of photocatalytic degradation mycotoxin graphene/TiO2And its preparation method and application
Background technique
Mycotoxin is some fungies, and such as aspergillus, Penicillium and Fusarium, what is generated during the growth process easily causes people It is very high to humans and animals toxicity with the secondary metabolite of animal pathological change and physiology metamorphosis.Existing 300 kinds of discovery so far true Verticillium toxin, wherein representative mycotoxin has Trichothecenes toxin (such as DON), zearalenone (ZEN), volt Horse toxin B1(FB1), aflatoxin (AFT), ochratoxin A (OTA) and T-2 toxin etc..Mycotoxin pollutes grain and feeding After material, into food chain, to influence breeding performonce fo animals and health of people.Due to mycotoxin chemistry, biology and toxicity It is varied to learn property, therefore its toxic effect difference is also very big, depends on it and take in level, exposure duration, animal species, body Synergistic effect etc. between mycotoxin is existed simultaneously in body situation and feed or food.But its common toxicity mainly causes DNA damage Two aspects of wound and cytotoxicity;Specifically, the effect of mycotoxin major toxicity includes carcinogenesis, genetoxic, teratogenesis Effect, hepatotoxicity, nephrotoxicity, genital disorders and immunosupress.The method effect of existing processing mycotoxin It is ideal not enough, it mainly include physical method, chemical method, absorption method and bioanalysis etc..Physical method detoxification is not thorough, Environmental costs It is high;Chemical method is fast rapid, but is easy residual noxious material, influences quality;Absorption method needs to carry out desorption processing, is also easy to produce two Secondary pollution;Biochemical method takes a long time, and cost is excessively high, and metabolite toxicity is unclear.Therefore, a kind of letter green to be developed is high The forward position detoxification technology of effect is expected to increase substantially the abatement effect of vomitoxin, reduces treatment cost.For ensureing national grain Food safety and human health have great importance.
Directly in-depth study has been obtained in terms of depth degradation organic pollutant using solar energy in photocatalysis technology, It is mild with reaction condition, solar energy can be made full use of, without secondary pollution, the advantages such as processing cost is low.Currently, photocatalysis technology Existing Main Scientific Issues are that quantum efficiency is not high and visible light activity is poor.It, must be anti-from photocatalysis more than solving the problems, such as The essence answered considers, first is that how to further suppress the recombination probability in light induced electron and hole, improves light-catalysed quantum efficiency Problem;Second is that how further to expand sun light absorption wave band, developing has the visible light even photocatalysis body of infrared optical response System.In photocatalytic system, the separation of charge and the migration of photo-generated carrier are the rate determining steps of reaction, but due to the loss of heat, The presence of the extraneous factors such as the defect of surface and body phase can be such that photoinduced electron and hole occurs compound.Therefore, it is urged to improve light The quantum efficiency for changing reaction selects suitable method of modifying to reduce electron-hole recombination rate and become the key point of research.
TiO2It is a kind of conventional ultra-violet photosensitiveness catalyst, since forbidden bandwidth (3.2eV) is wider, wave can only be absorbed in principle The long ultraviolet light for being shorter than 387nm, optical response range is narrow cannot be high using visible light, electron hole pair recombination rate, quantum efficiency compared with It is low, limit TiO2Large-scale application and development of the nano particle as photochemical catalyst.Therefore to TiO2Modified by nano particles is to mention Its high photocatalytic activity.But existing main problem includes: that quantum yield is relatively low, and spectral response range is narrow, point of photochemical catalyst It is difficult from recycling.Therefore, a kind of more efficient system is constructed to improve TiO2The activity and stability of nano particle are especially It is important.The present invention obtains a kind of hybrid material of photocatalytic degradation mycotoxin by simple, green preparation method graphene/TiO2, photocatalysis performance can be greatly improved.It will be expected to the removing neck in mycotoxin by means of the present invention Domain introduces a kind of new method, facilitates the mixing together for pushing mycotoxin control and field of functional materials, drops for mycotoxin Solution method provides part foundation and new approaches.
Summary of the invention
The first purpose of this invention is to provide a kind of hybrid material graphene/ of photocatalytic degradation mycotoxin TiO2
Second object of the present invention is to provide a kind of hybrid material graphene/ of photocatalytic degradation mycotoxin TiO2Preparation method.
Third object of the present invention is to provide a kind of hybrid material graphene/ of photocatalytic degradation mycotoxin TiO2Application in photocatalytic degradation mycotoxin.
In order to achieve the above objectives, the invention adopts the following technical scheme:
A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2, hybrid material graphene/TiO2 It mainly include TiO2Nano particle and its surface coated single-layer or multi-layer graphene film, it is by graphene oxide and TiO2It receives Rice grain is according to the ratio that mass ratio is 0.1-10:100 by made from hydrothermal synthesis method.
A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2Preparation method, include the following steps:
1) graphene oxide dispersion is first subjected to first time ultrasonic treatment, then by the graphene oxide after ultrasonic treatment Dispersion liquid carries out low-speed centrifugal processing, removes sub-cloud aggregation after centrifugal treating, obtains upper solution;The upper solution is carried out Then upper solution after ultrasonic treatment is carried out high speed centrifugation processing, removes upper layer after centrifugal treating by second of ultrasonic treatment Unstripped graphene oxide obtains the graphene oxide of removing;It disperses the graphene oxide after removing in deionized water, after It is continuous to carry out third time ultrasonic treatment, obtain the graphene oxide dispersion in single or multi-layer structure;
It 2) will be in the graphene oxide dispersion and TiO of single or multi-layer structure2Nano particle is mixed, and then carries out 4th time ultrasonic treatment makes TiO2Nano particle forms uniform nano-dispersed state, obtains mixture;Stone is aoxidized in the mixture Black alkene and TiO2The mass ratio of nano particle is 0.1-10:100;
3) mixture is subjected to hydro-thermal reaction, obtains hybrid material graphene/TiO after reaction2
Further, the actual conditions of the first time ultrasonic treatment do not limit, and graphene oxide dispersion can be made by referring to Form uniform dispersion liquid;The condition of second of ultrasonic treatment does not limit, and referring to can make to aoxidize in the upper solution Graphene is removed;The condition of the third time ultrasonic treatment does not limit, and refers to that the graphene oxide after capable of making removing is equal Even dispersion in deionized water, and removes graphene oxide after removing again;The condition of 4th ultrasonic treatment It does not limit, TiO can be made by referring to2Nano particle forms uniform nano-dispersed state;
Further, after hydro-thermal reaction, graphene oxide is reduced to graphene.
Graphene oxide and TiO is added by adjusting in the present invention2The mass ratio of nano particle, to adjust hybrid material graphene/TiO2The modification amount of surface graphene.
Further, the revolving speed of the low-speed centrifugal processing is 2000-5000r/min;The revolving speed of the high speed centrifugation processing For 8000-20000r/min.
Further, the concentration of the graphene oxide solution is 0.1-10mg/mL.
Further, the temperature of the hydro-thermal reaction is 160-180 DEG C.
Further, the time of the hydro-thermal reaction be 4-10h (such as: 4,5,6,7,8,9 or 10 h).
Further, single-layer graphene oxide with a thickness of 0.78nm.
Further, the TiO2The partial size of nano particle is 10-21nm;Preferably, the TiO2The partial size of nano particle is 21nm。
Further, multilayer of the present invention refers to the multilayer within five layers and five layers be made of single layer
The present invention is combined by ultrasonic treatment and centrifugal treating, and graphene oxide is carried out to the removing of layer structure, shape At the graphene oxide of single or multi-layer structure, then by hydro-thermal method in TiO2The stone of nano grain surface cladding layer structure Black alkene piece, to be prepared into hybrid material graphene/TiO2
A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2In photocatalytic degradation mycotoxin Using.
Further, the mycotoxin is deoxynivalenol, zearalenone, aflatoxin, volt horse Toxin, ochratoxin or T-2 toxin.
Further, a kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2In photocatalytic degradation fungi Application in toxin, it is realized by the following method:
1) by the hybrid material graphene/TiO2It is added in mycotoxin sample, is ultrasonically treated 0.5-1 h, then 0.5-1h is stirred, the first mixed liquor is obtained;
2) first mixed liquor is subjected to light degradation.
Further, light degradation is irradiated using the light source of wavelength X < 1000nm.
Further, the light degradation time is 120-300min.
Further, in the mycotoxin sample mycotoxin concentration >=0.1 μ g/kg.
It is further noted that if not otherwise specified, any range documented by the present invention includes end value and end value Between any numerical value and any subrange for being constituted with any number between end value or end value.
Beneficial effects of the present invention are as follows:
1, graphene oxide is carried out to the removing of layer structure by means of the present invention, then by hydro-thermal method in TiO2 Nano grain surface coats single-layer or multi-layer graphene film, to be prepared into hybrid material graphene/TiO2
2, the present invention has visible light-responded hybrid material graphene/TiO by hydro-thermal method preparation2, simple process, It is suitable for industrial mass production, and Photocatalyst is applied to degradative fungi toxin field there is very high answer With prospect and practical value.
Detailed description of the invention
Specific embodiments of the present invention will be described in further detail with reference to the accompanying drawing.
Fig. 1: (a) scheme for the SEM of GP0.3;(b) scheme for the TEM of GP0.3.
Fig. 2 is GP0.1, GP3.0, TiO2The FTIR of nano particle (P25) and graphene oxide (GO) figure.
Fig. 3 is experimental group, control group and blank group photocatalytic degradation deoxidation under conditions of ultraviolet wavelength λ=365nm The curve graph of nivalenol.
Fig. 4 be under conditions of ultraviolet wavelength λ=365nm, GP0.1, GP0.3, GP3.0, GP5.0, GP8.0 and The bar chart of GP10.0 photocatalytic degradation deoxynivalenol degradation rate.
Fig. 5 is the height of GP0.3 photocatalytic degradation deoxynivalenol when the light degradation time is extended to 300min Effect liquid phase chromatogram figure.
Specific embodiment
In order to illustrate more clearly of the present invention, the present invention is done further below with reference to preferred embodiments and drawings It is bright.It will be appreciated by those skilled in the art that specifically described content is illustrative and be not restrictive below, it should not be with this It limits the scope of the invention.
The materials, reagents and the like used in the following examples is commercially available unless otherwise specified.The present invention Used in reactant sodium nitrate, the concentrated sulfuric acid, potassium permanganate, multi-oxygen water, hydrochloric acid, acetonitrile, methanol etc. be pure, the mesh of commercially available analysis The standard items that degradation product mycotoxin is the purchase of Sigma company are marked, deionized water is homemade.
Using Flied emission LEO-1530 type scanning electron microscope and HITACHI HT7700 type transmission electron microscope observing graphene hydridization The pattern of material.
The analysis of structure of functional groups, the wave of scanning are carried out using the infrared spectrometer of German 700 type of Bruker VERTEX Number range is 4000-600cm-1, scanning resolution is set as 4cm-1
High performance liquid chromatography detection conditioned reference national standard " deoxynivalenol in GB/T 23503-2009 food Measurement immunoaffinity chromatography purify high performance liquid chromatography ", specific chromatographic condition can are as follows:: chromatographic column: C18 column (250mm × 4.6mm, 5 μm, xbridge);Mobile phase: methanol/water=20/80 (V/V);Flow velocity 1.0mL/min;25 DEG C of column temperature;Sample volume 10μL;UV detector, Detection wavelength 218nm.
Embodiment 1
1) hybrid material graphene/TiO2Preparation
The graphene oxide solution that concentration is 5mg/mL is taken out from 4 DEG C of refrigerator, is first carried out first time ultrasonic treatment, is made Graphene oxide dispersion forms uniform dispersion liquid;Then by the graphene oxide dispersion after ultrasonic treatment with 5000r/ The revolving speed of min carries out centrifugal treating, removes sub-cloud aggregation after centrifugal treating, obtains upper solution;The upper solution is carried out Second of ultrasonic treatment, removes graphene oxide in the upper solution;Then by the upper solution after ultrasonic treatment Centrifugal treating is carried out with the revolving speed of 10000r/min, the unstripped graphene oxide in upper layer is removed after centrifugal treating, obtains removing Graphene oxide;Graphene oxide 200mg after taking removing is scattered in 100mL deionized water, continues third time ultrasound Processing, the graphene oxide after making removing is evenly dispersed in deionized water, and shells the graphite oxide after removing again From;Obtain the graphene oxide dispersion in single or multi-layer structure that concentration is 2mg/mL;
It 2) is 2mg/mL in the graphene oxide dispersion of single or multi-layer structure and the TiO of 13g by 20mL concentration2 Nano particle is mixed, and stirring is to can't see big bulk TiO2Then the aggregation of nano particle carries out the 4th ultrasound Processing makes TiO2Nano particle forms uniform nano-dispersed state;By the mixture in 180 DEG C of progress hydro-thermal reaction 6h, reef knot Temperature fall is carried out after beam, obtains linen solid powder, and the linen solid powder is hybrid material graphene/ TiO2, i.e. (" 0.3 " in GP0.3 refers to the graphene oxide and TiO of addition to GP0.32The mass ratio of nano particle is 0.3: 100)。
In conjunction with Fig. 1 it is found that the micro details of (a) are shown, TiO2Nano grain surface has coated single-layer or multi-layer graphene Nanometer sheet, it is corresponding with the pattern details of GP0.3 of (b) reflection, it provides and finishes for the raising of the Photocatalytic Degradation Property of GP0.3 Advantage on structure.
Embodiment 2
Except by " the TiO of 13g in 1 step 3) of embodiment2Nano particle " is changed to " TiO of 0.5g2Nano particle " obtains Except GP8.0, other modes same as Example 1 prepare hybrid material graphene/TiO2
Embodiment 3
Except by " the TiO of 13g in 1 step 3) of embodiment2Nano particle " is changed to " TiO of 40g2Nano particle " obtains Except GP0.1;Other modes same as Example 1 prepare hybrid material graphene/TiO2
Embodiment 4
Except by " the TiO of 13g in 1 step 3) of embodiment2Nano particle " is changed to " TiO of 1.3g2Nano particle " obtains Except GP3.0, other modes same as Example 1 prepare hybrid material graphene/TiO2
Embodiment 5
Except by " the TiO of 13g in 1 step 3) of embodiment2Nano particle " is changed to " TiO of 0.8g2Nano particle " obtains Except GP5.0, other modes same as Example 1 prepare hybrid material graphene/TiO2
In conjunction with Fig. 2 it is found that in wave number 1734cm-1、1400cm-1、1230cm-1、1061cm-1With 1624 cm-1It is right respectively to locate It should be in the flexible vibration of C=O deformation vibration, OH deformation vibration, the stretching vibration of C-OH, the stretching vibration of C-O-C and its ring skeleton It is dynamic;In 1580cm-1Place corresponds to the skeletal vibration peak of graphene sheet layer structure, and the surface hydridization of graphene makes to be located at 900cm-1 Within two position 720cm-1With 675 cm-1TiO2Feature peak position, which dies down, to broaden;In addition, intensity and the position of usually characteristic peak The intensity for corresponding to chemical bond is moved, if characteristic peak remitted its fury, illustrates the remitted its fury of chemical bond, it is on the contrary then enhance.If feature Red shift occurs for peak, illustrates the remitted its fury of chemical bond;Conversely, if blue shift, the enhanced strength of chemical bond occur for characteristic peak;Cause This, the surface hybridism of graphene weakens the vibration of Ti-O key, graphene and TiO2Between the mutual of chemical bond has occurred Effect.
Embodiment 6
Except by " the TiO of 13g in 1 step 3) of embodiment2Nano particle " is changed to " nano particle of 0.4g ", obtain GP10 it Outside, other modes same as Example 1 prepare hybrid material graphene/ TiO2
7 hybrid material graphene/TiO of embodiment2To the shadow of photocatalytic degradation deoxynivalenol (DON) It rings
Experimental group: 1) GP0.3 of 25mg is added in DON aqueous solution that 50mL concentration be 15ppm, is first ultrasonically treated 0.5h is stirred for 0.5h, and GP0.3 is made to reach adsorption equilibrium, obtains the first mixed liquor;
2) using first mixed liquid concentration as initial concentration, then using wavelength X=365nm ultraviolet light to described First mixed liquor carries out light degradation 120min.It is sampled after degradation, centrifugal treating is carried out to sample, it is upper after taking centrifugation Clear liquid is put into brown liquid phase bottle, and brown liquid phase bottle is put into 4 DEG C of refrigerators and saves backup, and is examined using high performance liquid chromatography It surveys.
In conjunction with Fig. 3 it is found that GP0.3 is in light degradation 15min, degradation rate reaches 95%, as the light degradation time extends When to 30min, degradation rate reaches 100%, and without the P25 of hydridization in light degradation 30min, degradation rate is only 12%.
Control group 1: except by " the hybrid material graphene/TiO in experimental group2" change " nano particle TiO into2", except, Other modes identical with experimental group carry out, nano particle TiO2In light degradation 30min, degradation rate 12%.
Control group 2: except by " the hybrid material graphene/TiO in experimental group2" change " g-C into3N4" except, it is other with The identical mode of experimental group carries out, g-C3N4In light degradation 30min, degradation rate is only 3%.
Control group 3: except by " the hybrid material graphene/TiO in experimental group2" change into except " ZnO ", it is other with reality It tests the identical mode of group to carry out, for ZnO in light degradation 30min, degradation rate is only 6%.
Blank group: it takes in the DON aqueous solution that 50mL concentration is 15ppm, is first ultrasonically treated 0.5h, is stirred for 0.5h, then Pure photodissociation (Photolysis) 120min is carried out to DON aqueous solution using wavelength X=365nm ultraviolet light.Degradation terminates laggard Row sampling carries out centrifugal treating to sample, and the supernatant after taking centrifugation is put into brown liquid phase bottle, and brown liquid phase bottle is put into 4 DEG C of refrigerators save backup, and are detected using high performance liquid chromatography, and when light degradation 30min, degradation rate is only 45%.
The different hybrid material graphene/TiO of embodiment 82To photocatalytic degradation deoxynivalenol (DON) It influences
1) by the hybrid material graphene/TiO of 25mg2It is added in the DON aqueous solution that 50mL concentration is 15ppm, first It is ultrasonically treated 0.5h, 0.5h is stirred for, makes hybrid material graphene/TiO2Reach adsorption equilibrium, obtains the first mixed liquor;
2) using first mixed liquid concentration as initial concentration, then using wavelength X=365nm ultraviolet light to described First mixed liquor carries out light degradation 120min.It is sampled after degradation, centrifugal treating is carried out to sample, it is upper after taking centrifugation Clear liquid is put into brown liquid phase bottle, and brown liquid phase bottle is put into 4 DEG C of refrigerators and saves backup, and is examined using high performance liquid chromatography It surveys, testing result such as Fig. 4.
The hybrid material graphene/TiO2For prepared in embodiment 1 to 6 GP0.1, GP0.3, GP3.0, GP5.0, GP8.0 and GP10.0.
In conjunction with Fig. 4 it is found that illustrating suitable graphene modified TiO2Nano particle can promote TiO2The electronics of nano particle With the migration and separating rate in hole, to improve the ability of Visible Light Induced Photocatalytic deoxynivalenol;When the oxygen of addition When the mass ratio of graphite alkene and nano-photocatalyst is 0.3:100, the Photocatalytic activity of GP0.3 is best, works as light degradation When time is to 10min, GP0.3 photocatalytic activity has reached 96.4%, when increasing to 8% with the dosage of graphene, Apparent reduction occurs for GP8.0 Photocatalytic activity, and when ratio reaches 10%, the suction-operated of graphene increases, and makes to assist Show to enhance the effect of GP10.0 sample removal DON with effect.It can be seen that although graphene surface hydridization has Conducive to hybrid material graphene/TiO2The light induced electron on surface shifts, but excessive dosage will hinder TiO2Light inhale It receives, but promotes the enhancing of suction-operated.Therefore may determine that, graphene promote separation of charge and reduce optical absorption intensity it Between there are an equalization points.
Influence of the different light degradation times of embodiment 9 to GP0.3 photocatalytic degradation deoxynivalenol
1) GP0.3 prepared by the embodiment of 25mg 1 is added in the DON aqueous solution that 50mL concentration is 15ppm, is first surpassed Sonication 0.5h, is stirred for 0.5h, and GP0.3 is made to reach adsorption equilibrium, obtains the first mixed liquor;
2) using first mixed liquid concentration as initial concentration, then using wavelength X=365nm ultraviolet light to described First mixed liquor carries out light degradation, is sampled after degradation, carries out centrifugal treating to sample, the supernatant after taking centrifugation is put Enter in brown liquid phase bottle, brown liquid phase bottle is put into 4 DEG C of refrigerators and saves backup, and then investigates the different light degradation times pair The influence of GP0.3 photocatalytic degradation DON, is detected using high performance liquid chromatography.
The light degradation time be 0min, 5min, 10min, 15min, 30min, 60min, 120 min, 180min, 240min and 300min.
In conjunction with Fig. 5 it is found that GP0.3 is to DON significant effect under wavelength X=365nm ultraviolet light, in light degradation 15min Interior, degradation is complete, degradation rate 100%;DON intermediate product at 1.8min gradually increases with the extension of light degradation time Add;DON intermediate product at 5.2min when the light degradation time extends to 10min with completely disappearing.
Obviously, the above embodiment of the present invention be only to clearly illustrate example of the present invention, and not be pair The restriction of embodiments of the present invention may be used also on the basis of the above description for those of ordinary skill in the art To make other variations or changes in different ways, all embodiments can not be exhaustive here, it is all to belong to this hair The obvious changes or variations that bright technical solution is extended out are still in the scope of protection of the present invention.

Claims (8)

1. a kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2, which is characterized in that the hybrid material graphene/TiO2It mainly include TiO2Nano particle and its surface coated single-layer or multi-layer graphene film;
The hybrid material graphene/TiO2Preparation method, include the following steps: 1) that graphene oxide dispersion is advanced Row is ultrasonically treated for the first time, and graphene oxide dispersion is made to form uniform dispersion liquid;Then low-speed centrifugal processing, centrifugation are carried out Sub-cloud aggregation is removed after processing, obtains upper solution;The upper solution is carried out second to be ultrasonically treated, keeps the upper layer molten Graphene oxide is removed in liquid, then carries out high speed centrifugation processing again, the unstripped oxidation in upper layer is removed after centrifugal treating Graphene obtains the graphene oxide of removing;It disperses the graphene oxide of removing in deionized water, it is super to continue third time Sonication keeps the graphene oxide of removing evenly dispersed in deionized water, and is removed again, obtains in single-layer or multi-layer knot The graphene oxide dispersion of structure;Wherein, the revolving speed of the low-speed centrifugal processing is 2000-5000 r/min;The high speed from The revolving speed of heart processing is 8000-20000 r/min;
It 2) will be in the graphene oxide dispersion and TiO of single or multi-layer structure2Nano particle is mixed, and then carries out the 4th Secondary ultrasonic treatment makes TiO2Nano particle forms uniform nano-dispersed state, obtains mixture;Graphene oxide in the mixture And TiO2The mass ratio of nano particle is 0.1-10:100;
3) mixture is subjected to hydro-thermal reaction, obtains hybrid material graphene/TiO after reaction2
2. hybrid material graphene/TiO according to claim 12, which is characterized in that the graphene oxide dispersion Concentration be 0.1-10 mg/mL, the TiO2The partial size of nano particle is 10-21nm.
3. hybrid material graphene/TiO according to claim 12, which is characterized in that the temperature of the hydro-thermal reaction is 160-180 DEG C, the time of the hydro-thermal reaction is 4-10 h.
4. the hybrid material graphene/TiO of photocatalytic degradation mycotoxin as described in claim 12In photocatalytic degradation fungi Application in toxin.
5. application according to claim 4, which is characterized in that the mycotoxin is deoxynivalenol, jade Zearlenone, aflatoxin, fumonisin, ochratoxin or T-2 toxin.
6. application according to claim 4 or 5, which is characterized in that it is realized by the following method:
1) by the hybrid material graphene/TiO2It is added in mycotoxin sample, is ultrasonically treated 0.5-1 h, is stirred for 0.5-1 h obtains the first mixed liquor;
2) first mixed liquor is subjected to light degradation.
7. application according to claim 6, which is characterized in that the light degradation using 1000 nm of wavelength X < light source into Row irradiation;The light degradation time is 120-300 min.
8. application according to claim 6, which is characterized in that the concentration of mycotoxin in the mycotoxin sample >= 0.1μg/kg。
CN201610582809.9A 2016-07-22 2016-07-22 A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation method and application Active CN106166483B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610582809.9A CN106166483B (en) 2016-07-22 2016-07-22 A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation method and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610582809.9A CN106166483B (en) 2016-07-22 2016-07-22 A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation method and application

Publications (2)

Publication Number Publication Date
CN106166483A CN106166483A (en) 2016-11-30
CN106166483B true CN106166483B (en) 2019-03-19

Family

ID=58065516

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610582809.9A Active CN106166483B (en) 2016-07-22 2016-07-22 A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation method and application

Country Status (1)

Country Link
CN (1) CN106166483B (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2018159123A1 (en) * 2017-03-03 2018-09-07 パナソニックIpマネジメント株式会社 Method for manufacturing photocatalyst material, and photocatalyst material
CN109699867B (en) * 2019-01-08 2022-07-12 华中农业大学 Method for degrading patulin in fruit juice
CN110935477A (en) * 2019-12-02 2020-03-31 江南大学 Application of titanium-based composite material in photocatalytic degradation of mycotoxin
CN113057279A (en) * 2021-04-25 2021-07-02 上海市农业科学院 Treatment method of mycotoxin
CN113522337A (en) * 2021-07-13 2021-10-22 上海市农业科学院 Preparation method and application method of titanium-based nano material for photocatalytic degradation of DON
CN115430464A (en) * 2022-08-15 2022-12-06 河南工业大学 Photocatalyst for selectively degrading mycotoxin, preparation method and application thereof

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104128183B (en) * 2014-06-27 2017-01-18 南开大学 Nanoscale magnetic graphene composite material for efficient degradation of microcystic toxins and preparation and application thereof

Also Published As

Publication number Publication date
CN106166483A (en) 2016-11-30

Similar Documents

Publication Publication Date Title
CN106166483B (en) A kind of hybrid material graphene/TiO of photocatalytic degradation mycotoxin2And its preparation method and application
CN106311303B (en) A kind of hybrid material graphene/C of photocatalytic degradation mycotoxin3N4And its preparation method and application
Yang et al. Fouling of TiO2 induced by natural organic matters during photocatalytic water treatment: Mechanisms and regeneration strategy
Zeng et al. Enhancement of photocatalytic activity of TiO2 by immobilization on activated carbon for degradation of aquatic naphthalene under sunlight irradiation
Li et al. Synthesis of ion-imprinted chitosan-TiO2 adsorbent and its multi-functional performances
Hashimoto et al. Photocatalytic oxidation of nitrogen oxide over titania–zeolite composite catalyst to remove nitrogen oxides in the atmosphere
Kumar et al. Acceleration of photo-reduction and oxidation capabilities of Bi4O5I2/SPION@ calcium alginate by metallic Ag: Wide spectral removal of nitrate and azithromycin
Li et al. Exploring the photocatalytic conversion mechanism of gaseous formaldehyde degradation on TiO2–x-OV surface
Viet et al. Noble metal-doped graphitic carbon nitride photocatalyst for enhancement photocatalytic decomposition of antibiotic pollutant in wastewater under visible light
Doumic et al. Efficient removal of Orange G using Prussian Blue nanoparticles supported over alumina
Khan et al. Visible light active indigo dye/graphene/WO3 nanocomposites with excellent photocatalytic activity
Wang et al. In-situ preparation of Ti3C2/Ti3+-TiO2 composites with mosaic structures for the adsorption and photo-degradation of flowing acetaldehyde under visible light
Han et al. Oxidative degradation of tetracycline using peroxymonosulfate activated by cobalt-doped pomelo peel carbon composite
Mohammadiyan et al. Synthesis and characterization of a magnetic Fe3O4@ CeO2 nanocomposite decorated with Ag nanoparticle and investigation of synergistic effects of Ag on photocatalytic activity
Mahboob et al. Mesoporous LaVO4/MCM-48 nanocomposite with visible-light-driven photocatalytic degradation of phenol in wastewater
Ma et al. Ultrasonic-assisted efficient degradation of tetracycline over ZnO/BiOBr heterojunctions: Synergistic effect and role of oxidative species
Zhang et al. Facile synthesize hierarchical tubular micro-nano structured AgCl/Ag/TiO2 hybrid with favorable visible light photocatalytic performance
Rajah et al. Clopyralid degradation using solar-photocatalytic/ozone process with olive stone activated carbon
Fatimah et al. Functionalization of hydroxyapatite derived from cockle (Anadara granosa) shells into hydroxyapatite–nano TiO 2 for photocatalytic degradation of methyl violet
Jiang et al. Efficient degradation of cefotaxime by a UV+ ferrihydrite/TiO2+ H2O2 process: the important role of ferrihydrite in transferring photo‐generated electrons from TiO2 to H2O2
Channei et al. Adsorption and photocatalytic processes of mesoporous SiO2-coated monoclinic BiVO4
CN105642368B (en) A kind of modified TiO2/ CNTs composite catalysts and preparation method thereof
Setiawan et al. Removal of methylene blue using heterogeneous Fenton process with Fe impregnated kepok banana (Musa acuminate L.) peel activated carbon as catalyst
CN106311208B (en) A kind of hybrid material graphene/ZnO of photocatalytic degradation mycotoxin and its preparation method and application
Syazwani et al. Designing visible-light-driven photocatalyst of Ag 3 PO 4/CeO 2 for enhanced photocatalytic activity under low light irradiation

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CP01 Change in the name or title of a patent holder
CP01 Change in the name or title of a patent holder

Address after: 100037 No. 11 Million Village Street, Xicheng District, Beijing

Patentee after: Academy of Sciences, State Bureau of Food and Materials Reserve

Address before: 100037 No. 11 Million Village Street, Xicheng District, Beijing

Patentee before: Academy of State Grain Administration