CN109395781A - A kind of tin-antiomony oxide hydrogel and its preparation method and application with class Fenton photocatalysis characteristic - Google Patents

A kind of tin-antiomony oxide hydrogel and its preparation method and application with class Fenton photocatalysis characteristic Download PDF

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CN109395781A
CN109395781A CN201811377040.2A CN201811377040A CN109395781A CN 109395781 A CN109395781 A CN 109395781A CN 201811377040 A CN201811377040 A CN 201811377040A CN 109395781 A CN109395781 A CN 109395781A
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tin
antiomony oxide
hydrogel
antiomony
oxide hydrogel
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CN109395781B (en
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李亚拿
唐盛
孙俊
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Jiangsu University of Science and Technology
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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
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • 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
    • B01J35/20Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state
    • B01J35/23Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state in a colloidal state
    • 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
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • 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
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent
    • 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

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  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Water Supply & Treatment (AREA)
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Abstract

The invention discloses a kind of tin-antiomony oxide hydrogel and its preparation method and application with class Fenton photocatalysis characteristic, the tin-antiomony oxide hydrogel is mainly formed by slurry by tin-antiomony oxide nano particle, it is mixed with poly-vinyl alcohol solution, then self assembly is to get the tin-antiomony oxide hydrogel as composed by tin, antimony, oxygen and carbon.Sufficient raw of the present invention, production cost is low, material preparation process is simple, easy to operate, yield is high, repeated strong;Hydrogel shape is controllable, stability is high, can be recycled, and gained tin-antiomony oxide hydrogel has class Fenton photocatalysis property, can degradation of methylene blue in the presence of hydrogen peroxide under the irradiation of ultraviolet light, in the application that water pollution process field has great potential.

Description

A kind of tin-antiomony oxide hydrogel and preparation method thereof with class Fenton photocatalysis characteristic And application
Technical field
The present invention relates to a kind of tin-antiomony oxide hydrogel and its preparation method and application with class Fenton photocatalysis characteristic, Belong to the synthesis technical field of nanoanalysis material.
Background technique
Since 21st century, human society is increasingly developed, we are also faced with while human civilization progress Various threats of the survival and development.Energy crisis and problem of environmental pollution are exactly that two hang-ups to stand in the breach and people are existing In urgent problem, therefore numerous researchers are also dedicated to probing into novel effective energy and research control pollution Effective treating method.Heterogeneous Photocatalysis of Semiconductors is exactly that under the effect of the catalyst, the solar energy of absorption can be converted It for chemical energy, go on smoothly some reactions that could occur at high temperature also can under mild conditions.Therefore semiconductor Photocatalysis technology is with a wide range of applications, and numerous researchers have also carried out largely conductor photocatalysis material Research, such as TiO2、WO3、CdS、Ag3PO4, BiOX (X=Cl, Br and I) etc..But most semiconductor catalyst all exists The difficult problem of recycling.
Summary of the invention
Goal of the invention: the inherent shortcoming in order to overcome Conventional nano photochemical catalyst, the present invention provide a kind of with class Fenton Tin-antiomony oxide hydrogel of photocatalysis characteristic and preparation method thereof and catalytic applications, which can be in ultraviolet lighting In the case where be catalyzed hydrogen peroxide mineralising organic pollutant, and preparation method is simple, raw material economics, and recycle it is convenient.
Technical solution: to achieve the goals above, the invention adopts the following technical scheme:
A kind of tin-antiomony oxide hydrogel with class Fenton photocatalysis characteristic, mainly by tin-antiomony oxide nano particle institute The slurry of formation, mixes with poly-vinyl alcohol solution, and then self assembly is to get the oxygen as composed by tin, antimony, oxygen and carbon Change tin antimony hydrogel.
The tin-antiomony oxide nano particle is formed by slurry, is by adding into tin-antiomony oxide nano particle aqueous solution Triethylamine, stirring, is formed by tin-antiomony oxide nanometer slurry.
The preparation method of the tin-antiomony oxide hydrogel, comprising the following steps:
(1) it takes tin-antiomony oxide nano particle to be added to the water, then adds triethylamine, stirring forms tin-antiomony oxide nano slurry Body;
(2) it takes pva powder to be added to the water, is heated to being completely dissolved, form poly-vinyl alcohol solution;
(3) above-mentioned tin-antiomony oxide nanometer slurry and poly-vinyl alcohol solution are taken, is mixed well;
(4) it freezes, thaws, recycle for several times to get stable tin-antiomony oxide hydrogel.
It is preferred that:
The quality amount ratio of triethylamine and tin-antiomony oxide nano particle is 1:(11-15 in step (1)), tin-antiomony oxide nanometer It is 14-16% that the concentration of tin-antiomony oxide, which is mass fraction, in slurry, and stirring is using the stirring that is vortexed.
The concentration of poly-vinyl alcohol solution is 90-110g/L in step (2), and heating temperature is 93-97 degree.
The volumetric usage ratio 2:(1-4 of tin-antiomony oxide nanometer slurry and poly-vinyl alcohol solution in step (3)).
Freezing in step (4), thaws, recycles method for several times are as follows: -20 degree freezings 12 hours then take out thaw at RT 2 Hour, it recycles 3 times.
The tin-antiomony oxide hydrogel can be used as class Fenton photocatalyst applications, such as the tin-antiomony oxide hydrogel Hydrogen peroxide mineralising organic pollutant can be catalyzed under ultraviolet irradiation condition.
Hydrogel is the material inside one kind with hydrophilic radical, it can water-swellable, but it is not soluble in water.And It belongs to high molecular material and it is internal in three-dimensional structure.It can absorb water formation stereochemical structure after meeting water and will not It is destroyed.
The utility model has the advantages that compared with the existing technology, the invention has the following advantages that
(1) the tin-antiomony oxide hydrogel of the present invention with class Fenton photocatalysis characteristic is using self-assembly method legal system Standby, used material preparation process is simple, yield is high and reproducible.
(2) the tin-antiomony oxide hydrogel of the present invention with class Fenton photocatalysis characteristic is compared to traditional tin oxide Antimony nano particle has recycling convenient, reuses stable feature.
Detailed description of the invention
Fig. 1 is the powder single crystal diffraction figure of the tin-antiomony oxide hydrogel in embodiment 1-4 with class Fenton photocatalysis characteristic;
Fig. 2 is the shape appearance figure of the tin-antiomony oxide hydrogel in embodiment 1 with class Fenton photocatalysis characteristic;
Fig. 3 is the photocatalysis schematic diagram of the tin-antiomony oxide hydrogel in embodiment 1 with class Fenton photocatalysis characteristic;
Fig. 4 is the catalytic performance test figure of the tin-antiomony oxide hydrogel in embodiment 1 with class Fenton photocatalysis characteristic;
Fig. 5 is the photocatalysis loop test figure of the tin-antiomony oxide hydrogel in embodiment 1 with class Fenton photocatalysis characteristic;
Specific embodiment
Below in conjunction with the drawings and specific embodiments, further explanation is made to the present invention.
Embodiment 1
It weighs in the tin-antiomony oxide nano particle and 10ml centrifuge tube of 35% Sb doped amount of 0.525g, adds water to 3.5ml, 56 μ l triethylamines are added, the stirring that is vortexed forms tin-antiomony oxide nanometer slurry.It weighs a certain amount of pva powder and 250ml is added In water, 95 degree of oil bath heatings are configured to the poly-vinyl alcohol solution of 100g/L to being completely dissolved;It is molten to weigh configured polyvinyl alcohol Liquid 3.5ml is added in 35% tin-antiomony oxide slurry of 3.5ml, vortex mixed, ultrasound to no bubble.It is bladdery by not having uniformly Mixed solution is added in the cuvette that square side length in bottom surface is 1cm height 4cm.Cuvette is placed in -20 degree freezing in refrigerator 12 hours, then take out thaw at RT 2 hours.Circulation 3 times, forms stable tin-antiomony oxide hydrogel.It is put into upper layer refrigerator guarantor It deposits.
Embodiment 2
It weighs in the tin-antiomony oxide nano particle and 10ml centrifuge tube of 25% Sb doped amount of 0.525g, adds water to 3.5ml, 56 μ l triethylamines are added, the stirring that is vortexed forms tin-antiomony oxide nanometer slurry.A certain amount of pva powder is weighed to be added In 250ml water, 95 degree of oil bath heatings are configured to the poly-vinyl alcohol solution of 100g/L to being completely dissolved;Weigh configured poly- second Enolate solution 3.5ml is added in 25% tin-antiomony oxide slurry of 3.5ml, vortex mixed, ultrasound to no bubble.To not have uniformly The mixed solution of bubble is added in the cuvette that square side length in bottom surface is 1cm height 4cm.Cuvette is placed in -20 in refrigerator Degree freezing 12 hours, then takes out thaw at RT 2 hours.Circulation 3 times, forms stable tin-antiomony oxide hydrogel.It is put into upper layer Refrigerator saves.
Embodiment 3
It weighs in the tin-antiomony oxide nano particle and 10ml centrifuge tube of 15% Sb doped amount of 0.525g, adds water to 3.5ml, 56 μ l triethylamines are added, the stirring that is vortexed forms tin-antiomony oxide nanometer slurry.A certain amount of pva powder is weighed to be added In 250ml water, 95 degree of oil bath heatings are configured to the poly-vinyl alcohol solution of 100g/L to being completely dissolved;Weigh configured poly- second Enolate solution 3.5ml is added in 15% tin-antiomony oxide slurry of 3.5ml, vortex mixed, ultrasound to no bubble.To not have uniformly The mixed solution of bubble is added in the cuvette that square side length in bottom surface is 1cm height 4cm.Cuvette is placed in -20 in refrigerator Degree freezing 12 hours, then takes out thaw at RT 2 hours.Circulation 3 times, forms stable tin-antiomony oxide hydrogel.It is put into upper layer Refrigerator saves.
Embodiment 4
It weighs in the tin-antiomony oxide nano particle and 10ml centrifuge tube of 5% Sb doped amount of 0.525g, adds water to 3.5ml, then 56 μ l triethylamines are added, the stirring that is vortexed forms tin-antiomony oxide nanometer slurry.It weighs a certain amount of pva powder and 250ml is added In water, 95 degree of oil bath heatings are configured to the poly-vinyl alcohol solution of 100g/L to being completely dissolved;It is molten to weigh configured polyvinyl alcohol Liquid 3.5ml is added in 5% tin-antiomony oxide slurry of 3.5ml, vortex mixed, ultrasound to no bubble.To not have uniformly bladdery mixed Solution is closed to be added in the cuvette that square side length in bottom surface is 1cm height 4cm.Cuvette is placed in -20 degree freezing 12 in refrigerator Hour, then take out thaw at RT 2 hours.Circulation 3 times, forms stable tin-antiomony oxide hydrogel.It is put into the preservation of upper layer refrigerator.
Embodiment 5
It is same as Example 1, it the difference is that only as follows:
The quality amount ratio of triethylamine and tin-antiomony oxide nano particle is 1:11, tin-antiomony oxide nanometer slurry in step (1) The concentration of middle tin-antiomony oxide is that mass fraction is 14%.
The concentration of poly-vinyl alcohol solution is 90g/L in step (2), and heating temperature is 93 degree.
The volumetric usage of tin-antiomony oxide nanometer slurry and poly-vinyl alcohol solution ratio 2:1 in step (3).
Embodiment 6
It is same as Example 1, it the difference is that only as follows:
The quality amount ratio of triethylamine and tin-antiomony oxide nano particle is 1:15, tin-antiomony oxide nanometer slurry in step (1) The concentration of middle tin-antiomony oxide is that mass fraction is 16%.
The concentration of poly-vinyl alcohol solution is 110g/L in step (2), and heating temperature is 97 degree.
The volumetric usage of tin-antiomony oxide nanometer slurry and poly-vinyl alcohol solution ratio 1:2 in step (3).
Powder diffraction characterization is carried out to hydrogel in embodiment 1-4.Powder diffraction data collection is in Japanese Shimadzu It is completed on XRD6000 diffractometer, tube voltage 40Kv, tube current 30mA, uses graphite monochromatised Cu K alpha ray.Data collection Using the θ scan pattern of θ/2, continuous scanning is completed within the scope of 20 ° to 80 °, and scanning speed is 2 °/min.Powder diffraction result is shown in Fig. 1.Fig. 1 is the tin-antiomony oxide hydrogel XRD spectrum figure about different Sb dopings (5%, 15%, 25%, 35%).It is all not Tin-antiomony oxide hydrogel spectrum with Sb doping all shows identical SnO2(P42/mnm,JCPDS File Card No.41-1445) the characteristic peak of single-phase cubic rutile structure.In addition, there is no other related with Sb other than these characteristic peaks Additional peak, this show mix Sb element be successfully doped to SnO2There is no to SnO before after lattice2Structure cause obviously Variation.
Fig. 2 be embodiment 1 in class Fenton photocatalysis characteristic tin-antiomony oxide hydrogel pictorial diagram, from figure we It can be seen that it is the cuboid of 1cm that the prepared hydrogel come out, which is the ground side length of rule,.
Fig. 3 is that tin-antiomony oxide in embodiment 1 with class Fenton photocatalysis characteristic receives the photocatalysis schematic diagram of hydrogel.It will Hydrogel is cut into small pieces, and is placed in the methylene blue solution of 100ml 40mg/l, and 500 μ l hydrogen peroxide, ultraviolet light is added Carry out the class Fenton photocatalytic degradation to methylene blue solution.
Fig. 4 is the tin-antiomony oxide hydrogel catalytic degradation schematic diagram in embodiment 1 with class Fenton photocatalysis characteristic.From figure We can obviously observe in 4, and under the action of hydrogen peroxide and ultraviolet lighting is added, tin-antiomony oxide hydrogel is to methylene blue Solution produces apparent degradation, and ultra-violet absorption spectrum corresponding to the degradation with methylene blue solution is in top 664nm Place, which can obviously be observed from the 3.6 of 0min, is reduced to the 0 of 70min.This shows the tin-antiomony oxide water-setting synthesized in embodiment 1 Glue has good class Fenton photocatalysis property.
Fig. 5 is the tin-antiomony oxide hydrogel photocatalysis loop test figure in embodiment 1 with class Fenton photocatalysis characteristic.Phase With under condition and time, after having carried out 6 circulation class Fenton photocatalytic degradation methylene blues of monolithic hydrogel, methylene Blue degradation rate still can achieve 96%, illustrate the tin oxide with class Fenton photocatalysis characteristic synthesized in embodiment 1 Antimony hydrogel has recycling conveniently, the stable characteristic of performance.

Claims (9)

1. a kind of tin-antiomony oxide hydrogel with class Fenton photocatalysis characteristic, which is characterized in that it is mainly by tin-antiomony oxide Nano particle is formed by slurry, mixes with poly-vinyl alcohol solution, and then self assembly is to get by tin, antimony, oxygen and carbon institute group At the tin-antiomony oxide hydrogel.
2. the tin-antiomony oxide hydrogel according to claim 1 with class Fenton photocatalysis characteristic, which is characterized in that described Tin-antiomony oxide nano particle is formed by slurry, is stirred by adding triethylamine into tin-antiomony oxide nano particle aqueous solution, It is formed by tin-antiomony oxide nanometer slurry.
3. the preparation method of tin-antiomony oxide hydrogel of any of claims 1 or 2, which comprises the following steps:
(1) it takes tin-antiomony oxide nano particle to be added to the water, then adds triethylamine, stirring forms tin-antiomony oxide nanometer slurry;
(2) it takes pva powder to be added to the water, is heated to being completely dissolved, form poly-vinyl alcohol solution;
(3) above-mentioned tin-antiomony oxide nanometer slurry and poly-vinyl alcohol solution are taken, is mixed well;
(4) it freezes, thaws, recycle for several times to get stable tin-antiomony oxide hydrogel.
4. the preparation method of tin-antiomony oxide hydrogel according to claim 3, which is characterized in that triethylamine in step (1) Quality amount ratio with tin-antiomony oxide nano particle is 1:(11-15), and the concentration of tin-antiomony oxide is in tin-antiomony oxide nanometer slurry Mass fraction is 14-16%, and stirring is using the stirring that is vortexed.
5. the preparation method of tin-antiomony oxide hydrogel according to claim 3, which is characterized in that polyethylene in step (2) The concentration of alcoholic solution is 90-110g/L, and heating temperature is 93-97 degree.
6. the preparation method of tin-antiomony oxide hydrogel according to claim 3, which is characterized in that tin oxide in step (3) The volumetric usage ratio 2:(1-4 of antimony nanometer slurry and poly-vinyl alcohol solution).
7. the preparation method of tin-antiomony oxide hydrogel according to claim 3, which is characterized in that freezing in step (4), solution Freeze, recycle method for several times are as follows: -20 degree freezings 12 hours then take out thaw at RT 2 hours, recycle 3 times.
8. application of the tin-antiomony oxide hydrogel of any of claims 1 or 2 as class Fenton photochemical catalyst.
9. application according to claim 8, which is characterized in that the tin-antiomony oxide hydrogel is urged under ultraviolet irradiation condition Change the application of hydrogen peroxide mineralising organic pollutant.
CN201811377040.2A 2018-11-19 2018-11-19 Tin antimony oxide hydrogel with Fenton-like photocatalytic characteristic and preparation method and application thereof Active CN109395781B (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113210012A (en) * 2021-04-23 2021-08-06 江苏科技大学 Artificial single cell structure material and preparation method and application thereof

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1760139A (en) * 2005-09-01 2006-04-19 太原理工大学 Technique for treating organic substance difficukt to be degradated in water through opto-electronic electrode
CN104925853A (en) * 2015-06-04 2015-09-23 天津市职业大学 Stable nano antimony-doped tin dioxide hydrosol and preparation method thereof
CN105514447A (en) * 2016-01-13 2016-04-20 南京理工大学 Method for preparing antimony-doped tin dioxide aerogel three-dimensional electrode through normal pressure drying
CN106564937A (en) * 2016-10-20 2017-04-19 浙江工业大学 Preparation method of antimony-doped nanometer tin oxide (ATO) powder
CN106750391A (en) * 2015-11-24 2017-05-31 青岛智信生物科技有限公司 The preparation method of polyvinyl alcohol-stannic oxide/graphene nano composite aquogel

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1760139A (en) * 2005-09-01 2006-04-19 太原理工大学 Technique for treating organic substance difficukt to be degradated in water through opto-electronic electrode
CN104925853A (en) * 2015-06-04 2015-09-23 天津市职业大学 Stable nano antimony-doped tin dioxide hydrosol and preparation method thereof
CN106750391A (en) * 2015-11-24 2017-05-31 青岛智信生物科技有限公司 The preparation method of polyvinyl alcohol-stannic oxide/graphene nano composite aquogel
CN105514447A (en) * 2016-01-13 2016-04-20 南京理工大学 Method for preparing antimony-doped tin dioxide aerogel three-dimensional electrode through normal pressure drying
CN106564937A (en) * 2016-10-20 2017-04-19 浙江工业大学 Preparation method of antimony-doped nanometer tin oxide (ATO) powder

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
ZUQIANG XU: "Sunlight-Induced Photo-Thermochromic Supramolecular Nanocomposite Hydrogel Film for Energy-Saving Smart Window", 《SOL. RRL》 *
何晓伟: "PVA/锑搀杂二氧化锡纳米复合材料的结构与性能研究", 《合成纤维》 *
张文豪: "纳米锑掺杂二氧化锡(ATO) 水凝胶的水热法制备以及ATO 导电薄膜的透明和隔热性能", 《化学研究》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113210012A (en) * 2021-04-23 2021-08-06 江苏科技大学 Artificial single cell structure material and preparation method and application thereof
CN113210012B (en) * 2021-04-23 2023-08-22 江苏科技大学 Artificial single-cell structural material and preparation method and application thereof

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