CN107185501A - The preparation method of graphene oxide/nano titanium oxide/sodium alginate composite and application - Google Patents

The preparation method of graphene oxide/nano titanium oxide/sodium alginate composite and application Download PDF

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CN107185501A
CN107185501A CN201710450398.2A CN201710450398A CN107185501A CN 107185501 A CN107185501 A CN 107185501A CN 201710450398 A CN201710450398 A CN 201710450398A CN 107185501 A CN107185501 A CN 107185501A
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graphene oxide
nano titanium
titanium oxide
sodium alginate
oxide
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CN107185501B (en
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徐红波
赵越
高星星
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University of Science and Technology Liaoning USTL
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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
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • 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
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/46Materials comprising a mixture of inorganic and organic materials
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4806Sorbents characterised by the starting material used for their preparation the starting material being of inorganic character
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • B01J2220/4825Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
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  • Chemical Kinetics & Catalysis (AREA)
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Abstract

The present invention relates to the preparation method of graphene oxide/nano titanium oxide/sodium alginate composite, add graphene oxide into deionized water, obtain graphene oxide solution;Nano titanium oxide is added in graphene oxide solution, reaction solution is obtained;Reaction solution is made by graphene oxide/nano titanium oxide mixed reactant using hydro-thermal method or microwave method;Sodium alginate soln is added in graphene oxide/nano titanium oxide mixed reactant, is placed in water-bath and reacts, then naturally cool to room temperature;Reactant is washed for several times using deionized water and absolute ethyl alcohol respectively, and finished product is obtained after drying.Composite prepared by the present invention considerably improves its dispersiveness and stability, and with specific surface area is big, stability is good, good dispersion, absorption property is strong and absorption specificity is good, to heavy metal ions in sewage Pb2+Removal efficiency it is high, have good application prospect in sewage treatment area.

Description

The preparation method of graphene oxide/nano titanium oxide/sodium alginate composite with Using
Technical field
Heavy metal ions in sewage Pb is removed the present invention relates to one kind2+Medicament, more particularly to graphene oxide/nanometer two The preparation method of titanium oxide/sodium alginate composite and application.
Background technology
Graphene oxide is the oxide of graphene, compared with graphene, graphene oxide have abundant oxy radical, Good chemical modifiability and hydrophily, has relatively broad as a kind of excellent sorbing material in pollution control field Application prospect.But, have that absorption specificity is relatively low during Adsorption, antijamming capability is weaker in analysis applications, Powder is easily reunited simultaneously, stability is poor and causes secondary pollution problems.Nano titanium oxide has that specific surface area is big, absorption By force, conductibility is high, band gap can reconcile chemical stability it is good the advantages of, in photocatalysis, water process, sensing and the dye sensitization sun The fields such as energy battery have a extensive future.Sodium alginate, is called sodium alginate, is extracted from the sea-tangle or sargassum of brown algae A kind of natural polysaccharide carbohydrate, the characteristics of with nontoxic, good hydrophily, biocompatibility and non-secondary pollution, And sodium alginate heavy metal ion has stronger chelating removal ability.
Publication No. CN106423272A Chinese invention patent application discloses a kind of load type titania/oxidation stone Black alkene bead and preparation method and application, technical scheme advantage is:Raw material sources are extensive, preparation technology is simple Singly, industrialized production etc. is easily achieved, while this product has good photo catalytic reduction energy to the hexavalent chromium in waste water Power;But there is also problem, preparation process is more complicated, the bead of preparation is used to handle the chromium ion in waste water, can not locate Manage heavy metal in waste water lead ion.
The A of Chinese invention patent application publication number CN 105561963 disclose a kind of nano titanium oxide/graphene oxide Composite and preparation method and application, the composite specific surface area is big, and photocatalysis efficiency is high, to the absorption property of dyestuff Improve a lot;But operating procedure is cumbersome, it is unfavorable for realizing industrialized production, is not also applied to remove heavy metal in waste water Ion.Therefore, develop a kind of preparation method it is simple, can the composite of effectively Adsorption heavy metal ions in sewage have very much Practical application meaning.
The content of the invention
It is multiple that the technical problems to be solved by the invention are to provide a kind of graphene oxide/nano titanium oxide/sodium alginate The preparation method of condensation material, the composite is removal heavy metal ions in sewage Pb2+Medicament, with larger ratio surface Good and dispersed, the stronger absorption property of long-pending, preferable stability and preferable absorption specificity.
To achieve the above object, the present invention is realized using following technical scheme:
The preparation method of graphene oxide/nano titanium oxide/sodium alginate composite, is completed in the steps below:
Step one:Add graphene oxide into deionized water, low whipping speed is under 180r/min~500r/min 15min~45min is stirred, the graphene oxide solution that concentration is 0.5mg/mL~5mg/mL is obtained;By nano titanium oxide plus Enter into graphene oxide solution, the mass ratio of nano titanium oxide and graphene oxide is 1~5:1;Low whipping speed is 0.5h~1h is stirred under 180r/min~500r/min, reaction solution is obtained;
Step 2:Graphene oxide/nano-silica is made in the reaction solution for being obtained step one using hydro-thermal method or microwave method Change titanium mixed reactant;
Step 3:Sodium alginate is added in deionized water, low whipping speed be 180r/min~500r/min under stir 0.5h~2h is mixed, the sodium alginate soln that concentration is 5mg/mL~15mg/mL is obtained;Sodium alginate soln is added to step 2 In obtained graphene oxide/nano titanium oxide mixed reactant, it is placed in water-bath, is 40 DEG C~80 DEG C, stirs in temperature Mix speed to stir 0.5h~1h under the conditions of 180r/min~500r/min, then naturally cool to room temperature;Sodium alginate and oxidation The mass ratio of graphene/nanometer titanium dioxide mixed reactant is 0.75~3:1;
Step 4:Step 3 is made into reactant to wash for several times, then in temperature using deionized water and absolute ethyl alcohol respectively 12h~24h is dried at 40 DEG C~80 DEG C of degree, graphene oxide/nano titanium oxide/sodium alginate composite is obtained.
Graphene oxide described in step one is prepared by Hummers methods.
Hydro-thermal method described in step 2 is reaction solution is under conditions of 100 DEG C~180 DEG C in temperature, hydro-thermal reaction 5h~ 20h, then reactor is naturally cooled into room temperature, graphene oxide/nano titanium oxide mixed reactant is made.
Microwave method described in step 2 is reaction solution under conditions of microwave intensity is 2.0KW~10KW, microwave reaction 5min~40min;Reactor is naturally cooled into room temperature again, graphene oxide/nano titanium oxide mixed reactant is obtained.
The application of graphene oxide/nano titanium oxide/sodium alginate composite:
Take a certain amount of containing Pb2+Waste water, it is described to contain Pb2+The concentration of waste water is 1~400mg/L, by a certain amount of oxidation stone Black alkene/nano titanium oxide/sodium alginate composite is added to containing Pb2+Add 0.1~50g's in waste water, in every liter of waste water Graphene oxide/nano titanium oxide/sodium alginate composite, is 5~8 with the HCl and NaOH pH value for adjusting solution, reaction Temperature control is at 15~30 DEG C, 3~18h of magnetic agitation, then static 30min, and Pb in waste water is completed through membrane filtration2+Removal.
Above-mentioned composite removes heavy metal ions in sewage Pb2+Principle:
By the structure of graphene oxide/nano titanium oxide/sodium alginate composite, be first graphene oxide and The combination of inorganic nano material premium properties, not only substantially increases the specific surface area of material, and in neutral and faintly acid ring Under border, due to electrostatic interaction, nano titanium oxide and the electronegative functional group of surface of graphene oxide are by the heavy metal of positively charged Ion Pb2+Neutralize, with Pb2+Complex compound is formed, makes Pb2+Almost all is aggregated and precipitated;Again by graphene oxide/receive Addition sodium alginate prepares composite in rice titania solution, and sodium alginate both plays fixed effect as binding agent, Simultaneously again to Pb2+Absorption serve cooperative effect, the composite can be promoted to heavy metal ions in sewage Pb2+Suction Attached performance.
Compared with prior art, the beneficial effects of the invention are as follows:
1. composite prepared by the present invention considerably improves its dispersiveness and stability, adsorbent is not only overcome The shortcoming of secondary pollution can be caused by easily reuniting and remaining in water, and it is more beneficial for the solid-liquid point after absorption as macroscopic body From.The composite has that specific surface area is big, stability is good, good dispersion, absorption property is strong and absorption specificity is good, to sewage Middle heavy metal ion Pb2+Removal efficiency it is high, have good application prospect in sewage treatment area.
2. preparation method of the present invention is simple and easy to apply, mild condition, reproducible, raw material are easy to get, it is with low cost to prepare.
Brief description of the drawings
Fig. 1 is sweeping for graphene oxide/nano titanium oxide/sodium alginate composite prepared by the embodiment of the present invention 3 Retouch electron microscope picture.
Fig. 2 is graphene oxide/nano titanium oxide/sodium alginate composite of the preparation of the embodiment of the present invention 3 to Pb2+ Removal effect figure.
Embodiment
The embodiment to the present invention is further illustrated below in conjunction with the accompanying drawings:
Embodiment 1
The preparation method of present embodiment graphene oxide/nano titanium oxide/sodium alginate composite is by following What step was completed:
Step one:Add graphene oxide into deionized water, the concentration that stirring obtains graphene oxide solution is 0.5mg/mL;Then nano titanium oxide is added in 50mL 0.5mg/mL graphene oxide solutions, nano titanium oxide Mass ratio with graphene oxide is 5:1, stirring obtains reaction solution;
Step 2:Reaction solution is poured into hydrothermal reaction kettle, under conditions of temperature is 120 DEG C, hydro-thermal reaction 8h, then will Reactor naturally cools to room temperature, and graphene oxide/nano titanium oxide mixed reactant is made;
Step 3:Sodium alginate is added in deionized water, mixing speed is 180r/min~200r/min, stirring 0.5h, stirring obtains concentration 15mg/mL sodium alginate soln;30mL 15mg/mL sodium alginate solns are added to oxidation In graphene/nanometer titanium dioxide mixed reactant, it is placed in after being reacted in water-bath, is 50 DEG C in temperature, mixing speed is 30min is stirred under the conditions of 180r/min~200r/min, room temperature is cooled to;Sodium alginate and graphene oxide/nano-silica The mass ratio for changing titanium mixed reactant is 3:1;
Step 4:Step 3 is made into reactant to wash 3 times using deionized water and absolute ethyl alcohol respectively, then in temperature 14h is dried at 60 DEG C, graphene oxide/nano titanium oxide/sodium alginate composite is made.
Embodiment 2
The preparation method of present embodiment graphene oxide/nano titanium oxide/sodium alginate composite is by following What step was completed:
Step one:Add graphene oxide into deionized water, the concentration that stirring obtains graphene oxide solution is 5mg/mL;Then nano titanium oxide is added in 50mL 5mg/mL graphene oxide solutions, nano titanium oxide and oxygen The mass ratio of graphite alkene is 1:1, stirring obtains reaction solution;;
Step 2:Reaction solution is poured into reactor, under conditions of microwave intensity is 5KW, microwave reaction 10min;Again Reactor is naturally cooled into room temperature, graphene oxide/nano titanium oxide mixed reactant is obtained;
Step 3:Sodium alginate is added in deionized water, low whipping speed be 300r/min~330r/min under stir 0.5h is mixed, stirring obtains concentration 10mg/mL sodium alginate soln;75mL 10mg/mL sodium alginate solns are added to oxygen In graphite alkene/nano titanium oxide mixed reactant, be placed in after being reacted in water-bath, temperature be 60 DEG C, mixing speed be 1h is stirred under the conditions of 260r/min~300r/min, room temperature is cooled to;Sodium alginate and graphene oxide/nano titanium oxide The mass ratio of mixed reactant is 1.5:1;
Step 4:Step 3 is made into reactant to wash 4 times using deionized water and absolute ethyl alcohol respectively, then in temperature 12h is dried at 70 DEG C, graphene oxide/nano titanium oxide/sodium alginate composite is made.
Embodiment 3
The preparation method of present embodiment graphene oxide/nano titanium oxide/sodium alginate composite is by following What step was completed:
Step one:Add graphene oxide into deionized water, the concentration that stirring obtains graphene oxide solution is 3mg/mL;Then nano titanium oxide is added in 50mL 3mg/mL graphene oxide solutions, nano titanium oxide and oxygen The mass ratio of graphite alkene is 3:1, stirring obtains reaction solution;
Step 2:Reaction solution is poured into hydrothermal reaction kettle, under conditions of temperature is 150 DEG C, hydro-thermal reaction 16h, then Reactor is naturally cooled into room temperature, graphene oxide/nano titanium oxide mixed reactant is made.
Step 3:Sodium alginate is added in deionized water, low whipping speed be 400r/min~420r/min under stir 0.5h is mixed, stirring obtains concentration 5mg/mL sodium alginate soln;90mL 5mg/mL sodium alginate solns are added to oxidation In graphene/nanometer titanium dioxide mixed reactant, be placed in after being reacted in water-bath, temperature be 70 DEG C, mixing speed be 40min is stirred under the conditions of 230r/min~260r/min, room temperature is cooled to;Sodium alginate and graphene oxide/nano-silica The mass ratio for changing titanium mixed reactant is 0.75:1;
Step 4:Step 3 is made into reactant to wash 3 times using deionized water and absolute ethyl alcohol respectively, then in temperature 18h is dried at 55 DEG C, graphene oxide/nano titanium oxide/sodium alginate composite is made.
Scanning electron microscope diagram such as Fig. 1 of graphene oxide/nano titanium oxide/sodium alginate composite of preparation It is shown.
The application examples of the composite of embodiment 3
Compound concentration is 40mg/L Pb2+Solution is separately added into the oxygen of the preparation of 0.05g embodiments 3 in 50mL conical flasks Graphite alkene/nano titanium oxide/sodium alginate composite, is 6, reaction temperature with the HCl and NaOH pH value for adjusting solution Control carries out magnetic agitation 0.5h, 1h, 2h, 3h, 4h, 5h, 6h, then static 30min respectively at 25 DEG C, after membrane filtration Pb in solution is measured using atomic absorption spectrophotometer2+, experimental result is as shown in Figure 2.
As seen from the figure, graphene oxide/nano titanium oxide/sodium alginate composite is to Pb2+Removal effect is with the time Change.
Graphene oxide/nano titanium oxide/sodium alginate composite and Pb2+When reacting 0.5h, Pb2+Clearance is 39.2%;From 0.5h to 2h, Pb2+Clearance brings up to 93.5%, heavy metal ions in wastewater Pb from 39.2%2+By big portion Divide and remove;When reaction carries out 3h, clearance reaches 98.9%, continues to increase the reaction time, clearance is basically unchanged, now adsorbed Reaction reaches balance.
The specific surface area of graphene oxide/nano titanium oxide/sodium alginate composite is big, stability is good, dispersiveness Well, absorption property is strong and absorption specificity is good, to heavy metal ions in sewage Pb2+Removal efficiency it is high.
Described above is only the general principle of the present invention, and not the present invention is imposed any restrictions, every right according to the present invention It carries out equivalent variations and modification, within the category of the art of this patent protection scheme.

Claims (5)

1. the preparation method of graphene oxide/nano titanium oxide/sodium alginate composite, it is characterised in that by following steps It is rapid to complete:
Step one:Add graphene oxide into deionized water, low whipping speed is stirring under 180r/min~500r/min 15min~45min, obtains the graphene oxide solution that concentration is 0.5mg/mL~5mg/mL;Nano titanium oxide is added to In graphene oxide solution, the mass ratio of nano titanium oxide and graphene oxide is 1~5:1;Low whipping speed is 180r/ 0.5h~1h is stirred under min~500r/min, reaction solution is obtained;
Step 2:Graphene oxide/nano titanium oxide is made in the reaction solution for being obtained step one using hydro-thermal method or microwave method Mixed reactant;
Step 3:Sodium alginate is added in deionized water, low whipping speed is stirring under 180r/min~500r/min 0.5h~2h, obtains the sodium alginate soln that concentration is 5mg/mL~15mg/mL;Sodium alginate soln is added to step 2 system In the graphene oxide/nano titanium oxide mixed reactant obtained, it is placed in water-bath, is 40 DEG C~80 DEG C, stirring in temperature Speed is stirring 15min~1h under the conditions of 180r/min~500r/min, then naturally cools to room temperature;Sodium alginate and oxidation stone The mass ratio of black alkene/nano titanium oxide mixed reactant is 0.75~3:1;
Step 4:Step 3 is made into reactant to wash for several times, then in temperature 40 using deionized water and absolute ethyl alcohol respectively DEG C~80 DEG C at dry 12h~24h, obtain graphene oxide/nano titanium oxide/sodium alginate composite.
2. the preparation method of graphene oxide/nano titanium oxide/sodium alginate composite according to claim 1, Characterized in that, the graphene oxide described in described step one is prepared by Hummers methods.
3. the preparation method of graphene oxide/nano titanium oxide/sodium alginate composite according to claim 1, Characterized in that, it is water under conditions of 100 DEG C~180 DEG C that the hydro-thermal method described in described step two, which is reaction solution in temperature, Thermal response 5h~20h, then reactor is naturally cooled into room temperature, graphene oxide/nano titanium oxide mixed reactant is made.
4. the preparation method of graphene oxide/nano titanium oxide/sodium alginate composite according to claim 1, Characterized in that, the microwave method described in described step two is reaction solution under conditions of microwave intensity is 2.0KW~10KW, Microwave reaction 5min~40min;Reactor is naturally cooled into room temperature again, graphene oxide/nano titanium oxide mixing is obtained Reactant.
5. the application of graphene oxide/nano titanium oxide/sodium alginate composite according to claim 1:It is special Levy and be, comprise the following steps that:
Graphene oxide/nano titanium oxide/sodium alginate composite is added to containing Pb2+In waste water, containing Pb2+Waste water it is dense Spend for 1~400mg/L, every liter contains Pb2+0.1~50g graphene oxide/nano titanium oxide/sodium alginate is added in waste water Composite, is 5~8 with HCl and the NaOH pH value for adjusting solution, reaction temperature control at 15~30 DEG C, magnetic agitation 3~ 18h, then static 30min, Pb in waste water is completed through membrane filtration2+Removal.
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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107469772A (en) * 2017-10-13 2017-12-15 山东理工大学 A kind of method of heavy metal classes incretion interferent in removal reverse osmosis concentrated water
CN107761195A (en) * 2017-10-26 2018-03-06 青岛大学 A kind of lignin-base nano carbon fibre preparation method for electrode of super capacitor
CN109126647A (en) * 2018-09-08 2019-01-04 佛山市森昂生物科技有限公司 A kind of preparation method of graphene oxide-sodium alginate gel ball
CN109651860A (en) * 2018-12-24 2019-04-19 湖北航天化学技术研究所 A kind of graphene/nanometer titanium dioxide composite material and preparation method and application
CN111054395A (en) * 2019-12-10 2020-04-24 中国环境科学研究院 Visible-light-driven photocatalyst, and preparation method and application thereof
CN116386928A (en) * 2023-06-02 2023-07-04 山东科技大学 Sodium alginate/titanium dioxide composite porous electrode material and preparation method thereof
CN118329785A (en) * 2024-06-14 2024-07-12 东北师范大学 Detection bottle for simultaneously detecting glucose, uric acid and lactic acid in whole blood and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103123869A (en) * 2012-11-28 2013-05-29 华中科技大学 Method used for preparing nano titanium dioxide-graphene composite material provided with three-dimensional multi-hole structure and products
CN104226281A (en) * 2014-10-13 2014-12-24 江南大学 Composite hydrogel for adsorption of heavy metal ions and preparation method thereof
CN104759253A (en) * 2015-04-14 2015-07-08 中国广州分析测试中心 Graphene sponge used for enriching heavy metals or removing pollutants in water and preparation method of graphene sponge
CN104785177A (en) * 2015-03-23 2015-07-22 同济大学 Preparation method of alginate-graphene compound double-network gel beads
CN105688809A (en) * 2016-01-26 2016-06-22 西南科技大学 Preparing method for graphene oxide/titanium dioxide nanometer tube composite material

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103123869A (en) * 2012-11-28 2013-05-29 华中科技大学 Method used for preparing nano titanium dioxide-graphene composite material provided with three-dimensional multi-hole structure and products
CN104226281A (en) * 2014-10-13 2014-12-24 江南大学 Composite hydrogel for adsorption of heavy metal ions and preparation method thereof
CN104785177A (en) * 2015-03-23 2015-07-22 同济大学 Preparation method of alginate-graphene compound double-network gel beads
CN104759253A (en) * 2015-04-14 2015-07-08 中国广州分析测试中心 Graphene sponge used for enriching heavy metals or removing pollutants in water and preparation method of graphene sponge
CN105688809A (en) * 2016-01-26 2016-06-22 西南科技大学 Preparing method for graphene oxide/titanium dioxide nanometer tube composite material

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107469772A (en) * 2017-10-13 2017-12-15 山东理工大学 A kind of method of heavy metal classes incretion interferent in removal reverse osmosis concentrated water
CN107761195A (en) * 2017-10-26 2018-03-06 青岛大学 A kind of lignin-base nano carbon fibre preparation method for electrode of super capacitor
CN109126647A (en) * 2018-09-08 2019-01-04 佛山市森昂生物科技有限公司 A kind of preparation method of graphene oxide-sodium alginate gel ball
CN109651860A (en) * 2018-12-24 2019-04-19 湖北航天化学技术研究所 A kind of graphene/nanometer titanium dioxide composite material and preparation method and application
CN109651860B (en) * 2018-12-24 2021-06-11 湖北航天化学技术研究所 Graphene/nano titanium dioxide composite material and preparation method and application thereof
CN111054395A (en) * 2019-12-10 2020-04-24 中国环境科学研究院 Visible-light-driven photocatalyst, and preparation method and application thereof
CN116386928A (en) * 2023-06-02 2023-07-04 山东科技大学 Sodium alginate/titanium dioxide composite porous electrode material and preparation method thereof
CN116386928B (en) * 2023-06-02 2023-08-04 山东科技大学 Sodium alginate/titanium dioxide composite porous electrode material and preparation method thereof
CN118329785A (en) * 2024-06-14 2024-07-12 东北师范大学 Detection bottle for simultaneously detecting glucose, uric acid and lactic acid in whole blood and application thereof

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