CN106076378A - A kind of preparation method and application of titanium dioxide graphene oxide carbon composite (TiO2 GO AC) - Google Patents

A kind of preparation method and application of titanium dioxide graphene oxide carbon composite (TiO2 GO AC) Download PDF

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Publication number
CN106076378A
CN106076378A CN201610456286.3A CN201610456286A CN106076378A CN 106076378 A CN106076378 A CN 106076378A CN 201610456286 A CN201610456286 A CN 201610456286A CN 106076378 A CN106076378 A CN 106076378A
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titanium dioxide
graphene oxide
tio
composite
carbon
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李海涛
渠陆陆
王娜
李艳艳
朱根
张柯
王瑞雪
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Jiangsu Normal 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
    • B01J27/20Carbon compounds
    • B01J27/22Carbides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • 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
    • 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
    • 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

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

Abstract

The invention provides a kind of titanium dioxide graphene oxide carbon composite (TiO2GO AC) preparation method and application, belong to technical field of composite materials.Titanium dioxide (the TiO that this composite is modified with graphene oxide2GO) it is presoma, then uses mineral carbon load TiO2GO and obtain.There is the advantages such as photocatalytic activity is high, specific surface area is big.TiO2GO uses Ti O C chemical bonds, its photocatalysis effect and TiO2Compare and improve a lot.Activated carbon, as the porous adsorbent of micropore prosperity, has the strongest absorbability to dissolved organic matter in water, some polluter being difficult to biochemistry or oxidative degradation is also had good adsorption effect.Activated carbon is joined TiO2In GO composite so that the catalysis activity of this material improves further.Therefore, this titanium dioxide graphene oxide carbon composite is a kind of good light-catalyzed reaction catalyst.

Description

A kind of titanium dioxide-graphene oxide-carbon composite (TiO2-GO-AC) preparation Methods and applications
Technical field
The invention belongs to technical field of composite materials, relate to a kind of titanium dioxide-graphene oxide-carbon composite (TiO2-GO-AC) preparation method;The invention still further relates to the application of this titanium dioxide-graphene oxide-carbon composite.
Background technology
Titanium dioxide (TiO2) have that chemical stability is strong, nontoxic and low cost and other advantages, and by extensively
Pay close attention to.But TiO2Energy gap big (about 3.2 eV), it is impossible to make full use of solar energy, its light induced electron and hole Compound probability is big, so the most sub-efficiency is low, is nanoscale additionally, due to granular size, so being difficult to reclaim after making to be finished.Oxidation Graphene has that specific surface area is big, conducts electricity very well, the easy advantage such as preparation, is well suited as catalyst carrier, Graphene It is incorporated in semi-conducting material, plays their synergism, the photocatalysis performance of material will be effectively improved.TiO2-GO Use Ti-O-C chemical bonds, highly stable, its photocatalysis effect and TiO2Compare and improve a lot.Activated carbon is as micropore Flourishing porous adsorbent, has the strongest absorbability to dissolved organic matter in water, some is difficult to biochemistry or oxidation The polluter of degraded also has good adsorption effect.The manufacturing cost of activated carbon also tends to reduce, and active carbon adsorption technology exists Wastewater treatment industry is extensively applied both at home and abroad.Activated carbon is joined TiO2In-GO composite, can be given full play to them Synergism so that the catalysis activity of this material improves further.
Summary of the invention
The invention aims to overcome problems of the prior art, utilize the stability of Ti-O-C chemical bond, The preparation method and application of a kind of titanium dioxide-graphene oxide-carbon composite with highlight catalytic active are provided.
A kind of titanium dioxide-graphene oxide-carbon composite (TiO2-GO-AC) preparation method, be by titanium dioxide Titanium, graphene oxide and the mass ratio that activated carbon ratio is 5:20:4 are added to the water, and stir, are then added to hydro-thermal anti- Answer in still, at 180 DEG C, react 12h, after having reacted, sucking filtration, be dried to obtain titanium dioxide-graphene oxide-carbon composite wood Material.
Further, a kind of titanium dioxide-graphene oxide-carbon composite (TiO2-GO-AC) preparation method, institute The activated carbon stated first passes through pretreatment, through grinding, crosses 60-80 mesh sieve, takes proper amount of active carbon powder, add while stirring 1mol/L dust technology, after standing a few hours, filters off solution and the floating thing on upper strata, by remaining activated carbon through sucking filtration, washing After, put into baking oven, under conditions of 100 DEG C, be dried 2h, after taking-up, filter out the active carbon powder of 60-100 mesh with sieve, It is placed in exsiccator as standby.
A kind of titanium dioxide-graphene oxide-carbon composite can be as the photocatalyst of organic dyestuff.
Titanium dioxide-graphene oxide-carbon composite prepared by the present invention has that photocatalytic activity is high, specific surface area is big Etc. advantage.TiO2-GO uses Ti-O-C chemical bonds, highly stable, its photocatalysis effect and TiO2Compare and improve a lot. Activated carbon, as the porous adsorbent of micropore prosperity, has the strongest absorbability to dissolved organic matter in water, to some The polluter being difficult to biochemistry or oxidative degradation also has good adsorption effect.The manufacturing cost of activated carbon also tends to reduce, and lives Property charcoal adsorption technology wastewater treatment industry at home and abroad is extensively applied.Activated carbon is joined TiO2In-GO composite, Their synergism can be given full play to so that the catalysis activity of this material improves further.
Accompanying drawing explanation
Fig. 1 is TiO2The SEM figure of-GO-ACl.
Fig. 2 is TiO2The SEM figure of-GO-AC2.
Fig. 3 is TiO2The absorbance figure of-GO-ACl photocatalysis rhodamine B.
Fig. 4 is TiO2The absorbance figure of-GO-AC2 photocatalysis rhodamine B.
Fig. 5 is TiO2-GO-AC1、TiO2-GO-AC2、TiO2-GO、TiO2After catalysis, rhodamine B dulling luminosity ratio is relatively.
Fig. 6 is TiO2-GO-AC1、TiO2-GO-AC2、TiO2-GO、TiO2Rhodamine B absorbance block diagram after catalysis.
Detailed description of the invention
Below by specific embodiment, the preparation of the composite of the present invention and corresponding catalyst thereof is described further.
Embodiment 1
By ultrasonic for 31.25mlGO 1h, add 0.125g titania powder, add coal mass active carbon (being abbreviated as AC1), stirring 0.5h, is then transferred to 50ml hydrothermal reaction kettle by mixed liquor, puts into drying baker and reacts 12h at 180 DEG C.Sucking filtration after cooling, It is washed with water to there is no Cl-(checking with silver nitrate solution), then i.e. can get activated carbon supported dioxy after 60 DEG C of vacuum drying Change the composite photo-catalyst TiO that titanium-GO is formed2-GO-AC l)。
By 50 ml rhodamine Bs (2 × 10 during experiment-4Mol/L), during solution is placed in reactor, TiO is added2-GO-ACl granule 72.46mg.In black box, under the conditions of blowing air, stir 30 min, make rhodamine B balance in titanium dioxide granule surface adsorption, with After, in reactor, taking 0.5 ml serosity be centrifuged separating, in its supernatant, the concentration markers of rhodamine B is C0.Then open Opening light source and carry out light-catalyzed reaction, every 30 min sample 0.5 ml, sample liquid by centrifugation after, take supernatant detection rhodamine B dense Degree, is labeled as C, and total reaction time is 2 h, and after 40 min, degradation rate reaches 99.42%.
Embodiment 2
By ultrasonic for 31.25mlGO 1h, add 0.125g titania powder, add cocoanut active charcoal (being abbreviated as AC2) 0.025g, Stirring 0.5h, is then transferred to mixed liquor 50ml hydrothermal reaction kettle, puts into drying baker and react 12h at 180 DEG C.Take out after cooling Filter, is washed with water to do not have Cl-(checking with silver nitrate solution), then i.e. can get activated carbon supported two after 60 DEG C of vacuum drying The composite photo-catalyst TiO that titanium oxide is formed2-GO-AC2)。
By 50 ml rhodamine Bs (2 × 10 during experiment-4Mol/L), during solution is placed in reactor, TiO is added2-GO-AC2 granule 72.46mg.In black box, under the conditions of blowing air, stir 30 min, make rhodamine B balance in titanium dioxide granule surface adsorption, with After, in reactor, taking 0.5 ml serosity be centrifuged separating, in its supernatant, the concentration markers of rhodamine B is C0.Then open Opening light source and carry out light-catalyzed reaction, every 30 min sample 0.5 ml, sample liquid by centrifugation after, take supernatant detection rhodamine B dense Degree, is labeled as C, and total reaction time is 2 h, and after 40 min, degradation rate reaches 87.87%.

Claims (3)

1. a preparation method for titanium dioxide-graphene oxide-carbon composite, be by titanium dioxide, graphene oxide and Activated carbon ratio is that the mass ratio of 5:20:4 is added to the water, and stirs, is then added in hydrothermal reaction kettle, at 180 DEG C Lower reaction 12h, after having reacted, sucking filtration, is dried to obtain titanium dioxide-graphene oxide-carbon composite.
2. according to a kind of titanium dioxide-graphene oxide-carbon composite (TiO described in claims 12-GO-AC) Preparation method, described activated carbon first passes through pretreatment, through grinding, crosses 60-80 mesh sieve, takes active carbon powder, while stirring Add the dust technology of concentration 1mol/L, after standing a few hours, filter off solution and the floating thing on upper strata, by remaining activated carbon warp Sucking filtration, after washing, puts into baking oven, is dried 2h, after taking-up, filters out the work of 60-100 mesh with sieve under conditions of 100 DEG C Property carbon powder.
3. titanium dioxide-graphene oxide-carbon composite can be as the photocatalyst of organic dyestuff.
CN201610456286.3A 2016-06-22 2016-06-22 A kind of preparation method and application of titanium dioxide graphene oxide carbon composite (TiO2 GO AC) Pending CN106076378A (en)

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Cited By (17)

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Publication number Priority date Publication date Assignee Title
CN106824157A (en) * 2017-02-22 2017-06-13 山东圣泉新材料股份有限公司 A kind of modified composite titania material and preparation method thereof, application
CN107174919A (en) * 2017-06-28 2017-09-19 中国航发北京航空材料研究院 The composite mesopore carbosphere air purifying preparation that graphene is modified
CN107185489A (en) * 2016-12-30 2017-09-22 常州碳星科技有限公司 The preparation method of the sorbing material of Atmospheric Organic Pollutants
CN107321340A (en) * 2017-06-29 2017-11-07 南通大学 A kind of graphene composite photocatalyst aeroge of hierarchical porous structure and preparation method thereof
CN107362788A (en) * 2017-06-20 2017-11-21 四川大学 A kind of graphene oxide/titanium dioxide activated carbon three-dimensional composite material and preparation method thereof
CN108249655A (en) * 2018-02-02 2018-07-06 上海师范大学 Rotary-type photocatalysis-absorption-UF membrane concerted reaction device
CN108786729A (en) * 2018-06-06 2018-11-13 张小伏 The preparation method of mask graphene/active carbon in-situ plural gel adsorbent
CN108927225A (en) * 2018-06-27 2018-12-04 浙江工业大学膜分离与水处理协同创新中心湖州研究院 A kind of photocatalysis membrana preparation method for dyestuff degradation
CN109289777A (en) * 2018-12-10 2019-02-01 安徽万山红环保科技有限公司 A kind of waste-gas adsorbant
CN109772301A (en) * 2019-02-27 2019-05-21 知合环境(北京)有限责任公司 Modified ozone oxidation catalyst of a kind of graphene oxide and preparation method thereof
CN110142042A (en) * 2019-04-25 2019-08-20 东北大学秦皇岛分校 A kind of RGO/TiO2The preparation method and application of/Ag aerogel type photochemical catalyst
CN112138645A (en) * 2020-11-02 2020-12-29 上海第二工业大学 Glass fiber ball beam supported GO/TiO2Photocatalyst and preparation method thereof
CN112169784A (en) * 2020-09-23 2021-01-05 宁波石墨烯创新中心有限公司 Titanium dioxide/graphene/carbon composite material and preparation method and application thereof
CN112495361A (en) * 2020-12-22 2021-03-16 深圳笨鸟冰虫环保科技有限公司 Environment-friendly efficient composite photocatalyst
CN113307326A (en) * 2021-05-20 2021-08-27 江西善拓环境科技有限公司 Preparation of tungsten-based oxide/carbon-based nano composite hydrosol and application of tungsten-based oxide/carbon-based nano composite hydrosol in wastewater treatment
US11161094B2 (en) 2019-05-01 2021-11-02 Imam Abdulrahman Bin Faisal University Titania-carbon dot-reduced graphene oxide composites, their make, and use
CN114956269A (en) * 2022-05-25 2022-08-30 合肥工业大学 Method for treating antibiotic wastewater by electro-Fenton-like fluidized bed coupling membrane reaction

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Cited By (23)

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CN107185489A (en) * 2016-12-30 2017-09-22 常州碳星科技有限公司 The preparation method of the sorbing material of Atmospheric Organic Pollutants
CN106824157A (en) * 2017-02-22 2017-06-13 山东圣泉新材料股份有限公司 A kind of modified composite titania material and preparation method thereof, application
CN107362788A (en) * 2017-06-20 2017-11-21 四川大学 A kind of graphene oxide/titanium dioxide activated carbon three-dimensional composite material and preparation method thereof
CN107362788B (en) * 2017-06-20 2020-06-16 四川大学 Graphene oxide/titanium dioxide-activated carbon three-dimensional composite material and preparation method thereof
CN107174919A (en) * 2017-06-28 2017-09-19 中国航发北京航空材料研究院 The composite mesopore carbosphere air purifying preparation that graphene is modified
CN107174919B (en) * 2017-06-28 2020-06-02 中国航发北京航空材料研究院 Graphene modified composite mesoporous carbon microsphere air purifying agent
CN107321340A (en) * 2017-06-29 2017-11-07 南通大学 A kind of graphene composite photocatalyst aeroge of hierarchical porous structure and preparation method thereof
CN108249655A (en) * 2018-02-02 2018-07-06 上海师范大学 Rotary-type photocatalysis-absorption-UF membrane concerted reaction device
CN108249655B (en) * 2018-02-02 2021-07-06 上海师范大学 Rotary type photocatalysis-adsorption-membrane separation synergistic reaction device
CN108786729A (en) * 2018-06-06 2018-11-13 张小伏 The preparation method of mask graphene/active carbon in-situ plural gel adsorbent
CN108927225A (en) * 2018-06-27 2018-12-04 浙江工业大学膜分离与水处理协同创新中心湖州研究院 A kind of photocatalysis membrana preparation method for dyestuff degradation
CN109289777A (en) * 2018-12-10 2019-02-01 安徽万山红环保科技有限公司 A kind of waste-gas adsorbant
CN109772301A (en) * 2019-02-27 2019-05-21 知合环境(北京)有限责任公司 Modified ozone oxidation catalyst of a kind of graphene oxide and preparation method thereof
CN110142042A (en) * 2019-04-25 2019-08-20 东北大学秦皇岛分校 A kind of RGO/TiO2The preparation method and application of/Ag aerogel type photochemical catalyst
CN110142042B (en) * 2019-04-25 2022-02-08 东北大学秦皇岛分校 RGO/TiO2Preparation method and application of/Ag aerogel photocatalyst
US11161094B2 (en) 2019-05-01 2021-11-02 Imam Abdulrahman Bin Faisal University Titania-carbon dot-reduced graphene oxide composites, their make, and use
CN112169784A (en) * 2020-09-23 2021-01-05 宁波石墨烯创新中心有限公司 Titanium dioxide/graphene/carbon composite material and preparation method and application thereof
CN112169784B (en) * 2020-09-23 2023-04-07 宁波石墨烯创新中心有限公司 Titanium dioxide/graphene/carbon composite material and preparation method and application thereof
CN112138645A (en) * 2020-11-02 2020-12-29 上海第二工业大学 Glass fiber ball beam supported GO/TiO2Photocatalyst and preparation method thereof
CN112495361A (en) * 2020-12-22 2021-03-16 深圳笨鸟冰虫环保科技有限公司 Environment-friendly efficient composite photocatalyst
CN113307326A (en) * 2021-05-20 2021-08-27 江西善拓环境科技有限公司 Preparation of tungsten-based oxide/carbon-based nano composite hydrosol and application of tungsten-based oxide/carbon-based nano composite hydrosol in wastewater treatment
CN114956269A (en) * 2022-05-25 2022-08-30 合肥工业大学 Method for treating antibiotic wastewater by electro-Fenton-like fluidized bed coupling membrane reaction
CN114956269B (en) * 2022-05-25 2023-10-24 合肥工业大学 Method for treating antibiotic wastewater by electro-Fenton-like and fluidized bed coupling membrane reaction

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