CN108404896A - A kind of photochemical catalyst of Liquidity limit dyestuff - Google Patents

A kind of photochemical catalyst of Liquidity limit dyestuff Download PDF

Info

Publication number
CN108404896A
CN108404896A CN201810239500.9A CN201810239500A CN108404896A CN 108404896 A CN108404896 A CN 108404896A CN 201810239500 A CN201810239500 A CN 201810239500A CN 108404896 A CN108404896 A CN 108404896A
Authority
CN
China
Prior art keywords
sio
tio
photochemical catalyst
positive ion
efficient absorption
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.)
Granted
Application number
CN201810239500.9A
Other languages
Chinese (zh)
Other versions
CN108404896B (en
Inventor
李晓强
王纪冬
张家琳
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.)
Bosideng Down Wear Co ltd
Original Assignee
Jiangnan University
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 Jiangnan University filed Critical Jiangnan University
Priority to CN201810239500.9A priority Critical patent/CN108404896B/en
Publication of CN108404896A publication Critical patent/CN108404896A/en
Application granted granted Critical
Publication of CN108404896B publication Critical patent/CN108404896B/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
    • 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
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/103Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate comprising silica
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • B01J35/39
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/03Precipitation; Co-precipitation
    • B01J37/031Precipitation
    • B01J37/035Precipitation on carriers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • B01J37/086Decomposition of an organometallic compound, a metal complex or a metal salt of a carboxylic acid
    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

Abstract

The invention discloses a kind of photochemical catalysts of Liquidity limit dyestuff, belong to field of material technology.It is pore-foaming agent, absolute ethyl alcohol as solvent that the present invention, which is using polyvinylpyrrolidone (PVP), butyl titanate, tetraethyl orthosilicate, silane coupling agent KH560 are primary raw material, using sol-gal process precursor solution, then will be obtained after aging, drying, calcining can be with the TiO of the efficient absorption dye of positive ion2/SiO2Photochemical catalyst.The dye of positive ion that can effectively in adsorption aqueous solution of the present invention, is provided simultaneously with photocatalytic degradation effect, the catalyst of recycling can recycle after calcining.It can be used for the fields such as the decoloration of discarded dyeing waste water.

Description

A kind of photochemical catalyst of Liquidity limit dyestuff
Technical field
The present invention relates to a kind of photochemical catalysts of Liquidity limit dyestuff, belong to field of material technology.
Background technology
Textile industry will produce a large amount of dyeing waste waters, the complicated aromatic series of dyestuff in production process and its last handling process Structure makes them more stablize, it is difficult to be removed from waste water, the discharge of the dyeing waste water of unprocessed mistake can bring serious ring Border problem.The method of currently processed dyeing waste water has Physical, biodegradation technique and chemical method etc..Wherein, using most It is chemical method, including Coagulation Method, oxidizing process, electrochemical process and photocatalytic method etc..Photocatalytic degradation is because it is efficient, environmental protection, easily behaviour The advantages of making and become most promising one of hair method.
Photocatalyst starts from the 1970s, effectively being degraded by luminous energy is transformed into chemical energy organic Object.Wherein Photocatalytic Oxidation With Semiconductors technology is with efficient, low energy consumption, easy to operate, reaction condition is mild, non-secondary pollution The advantages that, effectively it can convert organic pollution to inorganic molecules, realization is completely inorganization, and the chloroform that can degrade, Many conventional methods such as Polychlorinated biphenyls, organic phosphorus compound are difficult to the substance removed.
Methylene blue is a kind of typical dye of positive ion, is normally used in various photocatalysis experiments and adsorption experiment. Researcher is more by polyurethane foam (PUFs), carbon nanotube (CNTs), the substances such as activated carbon and TiO2Photochemical catalyst In conjunction with method come improve the absorption property of photochemical catalyst make a return journey water removal in methylene blue to promote dyestuff removal rate.In order to Adsorption efficiency is improved, achievees the purpose that environmental protection, can be recycled, needs to prepare a kind of new catalyst that absorption property is promoted.
Invention content
The first purpose of the invention is to provide a kind of TiO of the efficient absorption dye of positive ion2/SiO2Photochemical catalyst, be with Polyvinylpyrrolidone (PVP) is pore-foaming agent, absolute ethyl alcohol is solvent, butyl titanate, tetraethyl orthosilicate, silane coupling agent KH560 is primary raw material, and precursor solution is prepared using sol-gal process, then will be prepared after its aging, drying, calcining The TiO of the efficient absorption dye of positive ion2/SiO2Photochemical catalyst.
In one embodiment, the TiO2/SiO2Middle TiO2Mass fraction be 45%-90%, SiO2Quality point Number is 0%-45%.
In one embodiment, the TiO2/SiO2Middle TiO2Mass fraction be 65%-85%, SiO2Quality point Number is 15%-35%.
In one embodiment, the TiO2/SiO2Middle TiO2Mass fraction be 65%, SiO2Mass fraction be 35%.
In one embodiment of the invention, Si:Ti:The molar ratio of PVC is 6~15:0~9:1~2.
In one embodiment of the invention, Si:Ti:The molar ratio of PVC is 9:0:1.
In one embodiment of the invention, Si:Ti:The molar ratio of PVC is 15:3:2.
In one embodiment of the invention, Si:Ti:The molar ratio of PVC is 6:3:1.
In one embodiment of the invention, Si:Ti:The molar ratio of PVC is 9:9:2.
In one embodiment, the aging is specifically:Stand 5-8 hours at room temperature.
In one embodiment, described dry is specifically:Gel is in 80 DEG C of baking oven until being completely dried.
In one embodiment, the calcining is to calcine 1-4h at 200-1000 DEG C.
In one embodiment, the calcining is to calcine 2h at 600 DEG C.
Second object of the present invention is to provide a kind of TiO of the efficient absorption dye of positive ion2/SiO2The system of photochemical catalyst Preparation Method specifically includes:
(1) KH560 is added in salpeter solution;Later, tetraethyl orthosilicate and/or butyl titanate is added, is rubbed You are than being 6~15:0~9 silicon and the mixed solution of titanium;
(2) using absolute ethyl alcohol as solvent, the PVP/ ethanol solutions of 0.08g/mL are configured, and under magnetic stirring by it It is added in mixed solution obtained in the previous step;Solution magnetic agitation after a certain period of time, obtains precursor solution;
(3) precursor solution is obtained into colloidal sol in aging 5-8 hours at room temperature, the colloidal sol after aging is placed in 80 DEG C of baking oven Middle drying obtains xerogel, is then ground to powder;
(4) powdered xerogel is calcined into 1-4h under 200-1000 DEG C of high temperature, to completely remove residual in the solution PVP, obtained product is by further grinding.
The present invention also provides application of the catalyst in terms of Liquidity limit dyestuff.
In one embodiment of the invention, the application includes carrying out decolorization to waste water.
Advantages of the present invention and effect:
(1) TiO of the invention2/SiO2Photochemical catalyst, it is strong, recyclable sharp simultaneously with adsorption rate height, photo-catalysis capability With the advantages that, adsorption rate remains at 86% or more after recycling 5 times, and degradation rate approach 100% can be used for dyeing waste water The fields such as decoloration.
(2) the method for the present invention, by effectively controlling TiO2、SiO2Ratio and calcination temperature etc., have obtained function admirable TiO2/SiO2
(3) the method for the present invention it is easy, it is easily-controllable, can flexible operating.
Description of the drawings
Fig. 1 is TiO2/SiO2Photochemical catalyst preparation flow figure;
Fig. 2 a are the TiO that the embodiment of the present invention 2 is prepared2/SiO2Photochemical catalyst electron micrograph;2b is to implement Absorption degradation curve of the example 2 to the 20mg/L methylene blue solutions of 60ml;
Fig. 3 a are absorption and light degradation reaction unit;3b is embodiment 2 and reference examples to methylene blue solution absorption degradation Curve.
Specific implementation mode
As shown in Figure 1, for the TiO of the present invention2/SiO2Photochemical catalyst preparation flow figure.Using PVP as pore-foaming agent, absolute ethyl alcohol For solvent, butyl titanate, tetraethyl orthosilicate etc. are raw material, and precursor sol is prepared using sol-gal process.It is small by 6 When aging obtain gel, in 80 DEG C of baking oven drying obtain xerogel.Then, by the xerogel after grinding through 200-1000 DEG C calcining, obtain TiO2/SiO2Material obtains final photocatalyst powder by further grinding.
To obtained TiO2/SiO2Photochemical catalyst carries out absorption property test, and test method is as follows:
The absorption of sample and light degradation property are tested using the test device in Fig. 3.Sample is placed in reactor In, certain density aqueous solution of methylene blue is injected in reactor by peristaltic pump, peristaltic pump is opened and is recycled.In dark It is adsorbed under environment 40 minutes, then opens ultraviolet lamp and carry out light degradation test.The usage amount of sample is 0.1g, methylene in test Blue aqueous solution usage amount is 60mL, initial concentration 20mg/L.
Test result shows that sample can adsorb 88% methylene blue for 40 minutes.60 minutes or so light degradation stage Time can be degradable the methylene blue of remainder.
Embodiment 1
TiO is prepared as follows2/SiO2Photochemical catalyst:
(1) solution A is prepared:The KH560 of 1.89g is added in the aqueous solution of nitric acid (pH=2.3) of 0.36ml;Later, above Tetraethyl orthosilicate, the butyl titanate that 1 stoichiometric ratio of table is sequentially added in solution, obtaining 6mL, to contain silicon, the mixing of titanium molten Liquid.
(2) 12ml polyvinylpyrrolidones/ethanol solution is prepared, and it is added under magnetic stirring to solution A In.
(3) precursor solution is stood to aging at room temperature and obtains colloidal sol within 5-8 hours, the colloidal sol after aging is placed in 80 DEG C Drying obtains xerogel in baking oven, is then ground to powder;
(4) powdered xerogel is calcined into 1-4h under 600 DEG C of high temperature, to remove PVP and other organic matters, obtained Product finally obtains different TiO by further grinding2、SiO2The TiO of ratio2/SiO2Powder.
Wherein, different TiO2、SiO2, PVP ratios composition of raw materials under (table 1).
1 difference TiO of table2/SiO2Ti, Si, PVP ratio in photochemical catalyst
Embodiment 2
(1) solution A is prepared:The KH560 of 1.89g is added in the aqueous solution of nitric acid (pH=2.3) of 0.36ml;Later, above Tetraethyl orthosilicate, the butyl titanate that 1 stoichiometric ratio of table is sequentially added in solution, obtaining 6mL, to contain silicon, the mixing of titanium molten Liquid, wherein Ti:The molar ratio of Si is 2:1.
(2) after, prepare 12ml polyvinylpyrrolidones/ethanol solution, and it is added under magnetic stirring to In solution A, make Si:The molar ratio of PVP is 3:1.
(3) precursor solution is stood to aging at room temperature and obtains colloidal sol within 5-8 hours, the colloidal sol after aging is placed in 80 DEG C Drying obtains xerogel in baking oven, is then ground to powder;
(4) 1-4h will be calcined under powdered xerogel at the temperatures shown in table 2 high temperature, had to remove PVP and other Machine object, obtained product finally obtain different TiO by further grinding2、SiO2The TiO of ratio2/SiO2Powder.
The different calcination temperatures of table 2
Absorption and light degradation experiment carry out in the homemade reactor (such as Fig. 3 a) for having cycle vermiculator.Specific steps It is as follows:
(1) aqueous solution of methylene blue that 60mL initial concentrations are 20mg/L is placed with 0.1g TiO by peristaltic pump sucking2/ SiO2In the reaction unit of powder;
(2) peristaltic pump is opened, 40min is adsorbed under dark surrounds;
(3) after adsorbing, the high-pressure sodium lamp of 250W is opened as light degradation light source, it is molten that 5mL is extracted in certain intervals Liquid measures its concentration using UV-1800 ultraviolet-visible light fluophotometers, and the solution after measurement is put back to reaction unit and continued Light degradation
(4) after measured, the final decoloration performance that the sample obtained under distinct methods obtains is as shown in table 3.
Table 3TiO2/SiO2Photochemical catalyst adsorption capacity and light degradation aptitude tests result
Note:Adsorption rate is that 40 minutes obtained experimental datas are adsorbed under dark surrounds, and degradation rate is 60 minutes gained of light degradation Experimental data.
Cycle carries out absorption to sample after experiment after centrifugation, filtering, drying, 400 DEG C of calcinings and light degradation is tested, sample The results are shown in Table 4 for 3 five loop tests of product.
Experimental result is shown, is adsorbed and the TiO after light degradation experiment2/SiO2Powder still has excellent by calcination processing Absorption and degradation capability.
The TiO of the present invention2/SiO2Photochemical catalyst is high simultaneously with adsorption rate, photo-catalysis capability is strong, can be recycled etc. Advantage can be used for the fields such as decolorizing printing and dyeing waste water.
Reference examples
In addition, inventor compares the absorption of (table 5) sample and light degradation property under different material formula, as a result such as Fig. 3 b It is shown.Wherein, specific experiment condition is compared with the parameter of embodiment 2, and only material composition is different.
5 different material ingredient of table
Note:" √ " indicates that addition, "-" expression are not added.
Inventor tests absorption and the light degradation property of embodiment 2 and reference examples using the identical test methods of Fig. 3 a, Its result is as shown in Figure 3b.PVP is added in material can promote the adsorption capacity of material, in order to illustrate PVP in material preparation Play the role of pore-foaming agent, the pore structure of material is analyzed, BET specific surface area test result is as shown in table 6.Its result Pore-foaming agent can be played the role of really by being shown in addition PVP in collosol and gel, and the change of this microstructure improves material Adsorption capacity.
Table 6BET specific surface area test results
Although the present invention has been described by way of example and in terms of the preferred embodiments, it is not limited to the present invention, any to be familiar with this skill The people of art can do various change and modification, therefore the protection model of the present invention without departing from the spirit and scope of the present invention Enclosing be subject to what claims were defined.

Claims (10)

1. a kind of TiO of the efficient absorption dye of positive ion2/SiO2Photochemical catalyst, which is characterized in that be with polyvinylpyrrolidone Pore-foaming agent, absolute ethyl alcohol are solvent, and butyl titanate, tetraethyl orthosilicate, silane coupling agent KH560 are primary raw material, are used Sol-gal process prepares precursor solution, then will prepare the efficient absorption dye of positive ion after its aging, drying, calcining TiO2/SiO2Photochemical catalyst.
2. the TiO of the efficient absorption dye of positive ion according to claim 12/SiO2Photochemical catalyst, which is characterized in that described TiO2/SiO2Middle TiO2Mass fraction be 45%-90%, SiO2Mass fraction be 0%-45%.
3. the TiO of the efficient absorption dye of positive ion according to claim 12/SiO2Photochemical catalyst, which is characterized in that described TiO2/SiO2Middle TiO2Mass fraction be 65%-85%, SiO2Mass fraction be 15%-35%.
4. according to the TiO of any efficient absorption dye of positive ion of claims 1 to 32/SiO2Photochemical catalyst, feature exist In Si:Ti:The molar ratio of PVC is 6~15:0~9:1~2.
5. the TiO of the efficient absorption dye of positive ion according to claim 12/SiO2Photochemical catalyst, which is characterized in that described Aging is to stand 5-8 hours at room temperature.
6. the TiO of the efficient absorption dye of positive ion according to claim 12/SiO2Photochemical catalyst, which is characterized in that described Drying is completely dried in 60~80 DEG C be dried to.
7. the TiO of the efficient absorption dye of positive ion according to claim 12/SiO2Photochemical catalyst, which is characterized in that described Calcining is to calcine 1-4h at 200-1000 DEG C.
8. a kind of TiO of the efficient absorption dye of positive ion2/SiO2The preparation method of photochemical catalyst, which is characterized in that specific steps Including:
(1) KH560 is added in salpeter solution;Later, tetraethyl orthosilicate and/or butyl titanate is added, obtains molar ratio It is 6~15:0~9 silicon and the mixed solution of titanium;
(2) using absolute ethyl alcohol as solvent, 0PVP/ ethanol solutions are configured, and it is added under magnetic stirring to step (1) In obtained mixed solution;
(3) mixed solution 5~8h of aging at room temperature that step (2) obtains, is placed in 60~80 DEG C of drying and obtains xerogel, grinding At powder;
(4) powdered xerogel is calcined to 1~4h under 200-1000 DEG C of high temperature, is remained in the solution with completely removing PVP, obtained product is by further grinding.
9. the TiO of any efficient absorption dye of positive ion of claim 1~82/SiO2Photochemical catalyst is in Liquidity limit Application in terms of dyestuff.
10. a kind of method to waste water decoloring processing, which is characterized in that it is any described to add claim 1~8 into waste water The TiO of the efficient absorption dye of positive ion2/SiO2Photochemical catalyst carries out decolorization.
CN201810239500.9A 2018-03-22 2018-03-22 Photocatalyst for adsorbing cationic dye Active CN108404896B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810239500.9A CN108404896B (en) 2018-03-22 2018-03-22 Photocatalyst for adsorbing cationic dye

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810239500.9A CN108404896B (en) 2018-03-22 2018-03-22 Photocatalyst for adsorbing cationic dye

Publications (2)

Publication Number Publication Date
CN108404896A true CN108404896A (en) 2018-08-17
CN108404896B CN108404896B (en) 2020-10-09

Family

ID=63133266

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810239500.9A Active CN108404896B (en) 2018-03-22 2018-03-22 Photocatalyst for adsorbing cationic dye

Country Status (1)

Country Link
CN (1) CN108404896B (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111359621A (en) * 2020-03-09 2020-07-03 南昌航空大学 Photocatalytic degradation composite particle and preparation method and application thereof
CN111514942A (en) * 2019-02-01 2020-08-11 尚国龙 Formaldehyde scavenging agent and preparation method thereof
CN111530411A (en) * 2020-05-13 2020-08-14 合肥学院 Preparation method of modified silicon dioxide composite adsorption material and application of modified silicon dioxide composite adsorption material in treatment of mercury-containing sewage

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103071478A (en) * 2011-10-25 2013-05-01 上海纳米技术及应用国家工程研究中心有限公司 Photocatalytic material used for treatment of dye wastewater and preparation method thereof
US20130153483A1 (en) * 2011-12-16 2013-06-20 Franca Morazzoni Photocatalytic composite material
CN105000625A (en) * 2015-07-16 2015-10-28 黄冈师范学院 Dye wastewater photocatalytic treatment method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103071478A (en) * 2011-10-25 2013-05-01 上海纳米技术及应用国家工程研究中心有限公司 Photocatalytic material used for treatment of dye wastewater and preparation method thereof
US20130153483A1 (en) * 2011-12-16 2013-06-20 Franca Morazzoni Photocatalytic composite material
CN105000625A (en) * 2015-07-16 2015-10-28 黄冈师范学院 Dye wastewater photocatalytic treatment method

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
JIDONG WANG ET AL.: "Er-doped titanium dioxide/silicon dioxide fibres with enhanced photodegradation performance", 《MICRO & NANO LETTERS》 *
WEIYANG DONG ET AL.: "Synchronous role of coupled adsorption and photocatalytic oxidation on ordered mesoporous anatase TiO2–SiO2 nanocomposites generating excellent degradation activity of RhB dye", 《APPLIED CATALYSIS B: ENVIRONMENTAL》 *
王忠华: "以聚乙烯吡咯烷酮K30为模板剂合成介孔二氧化钛", 《乙醛醋酸化工》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111514942A (en) * 2019-02-01 2020-08-11 尚国龙 Formaldehyde scavenging agent and preparation method thereof
CN111359621A (en) * 2020-03-09 2020-07-03 南昌航空大学 Photocatalytic degradation composite particle and preparation method and application thereof
CN111530411A (en) * 2020-05-13 2020-08-14 合肥学院 Preparation method of modified silicon dioxide composite adsorption material and application of modified silicon dioxide composite adsorption material in treatment of mercury-containing sewage
CN111530411B (en) * 2020-05-13 2022-04-19 合肥学院 Preparation method of modified silicon dioxide composite adsorption material and application of modified silicon dioxide composite adsorption material in treatment of mercury-containing sewage

Also Published As

Publication number Publication date
CN108404896B (en) 2020-10-09

Similar Documents

Publication Publication Date Title
Hsieh et al. Adsorption and visible-light-derived photocatalytic kinetics of organic dye on Co-doped titania nanotubes prepared by hydrothermal synthesis
CN106732818B (en) Double layer hollow material based on titanium dioxide and preparation method thereof and the application in hydrogen sulfide photocatalysis treatment
Ghosh et al. Preparation of Cu nanoparticle loaded SBA-15 and their excellent catalytic activity in reduction of variety of dyes
Yuan et al. Removal of organic dye by air and macroporous ZnO/MoO3/SiO2 hybrid under room conditions
CN104226337B (en) A kind of graphene-supported sheet molybdenum disulfide nano compound and preparation method thereof
Zhu et al. Preparation and characterization of Cu2O–ZnO immobilized on diatomite for photocatalytic treatment of red water produced from manufacturing of TNT
CN103934008B (en) A kind of preparation method of galapectite load silver phosphate photocatalyst
Sun et al. Engineering composition-tunable 3D hierarchical bismuth oxyiodides heterojunctions: Ionic liquid-assisted fabrication with strong adsorption ability and enhanced photocatalytic properties
CN108404896A (en) A kind of photochemical catalyst of Liquidity limit dyestuff
CN108579779A (en) A kind of three-dimensional composite material, preparation method and the application in the removal of water pollutant visible light photocatalytic degradation
Tsai et al. Preparation of TiN–TiO2 composite nanoparticles for organic dye adsorption and photocatalysis
Jafari et al. The role of adsorption in the photocatalytic decomposition of Orange II on carbon-modified TiO2
Zou et al. Fabrication and dye removal performance of magnetic CuFe2O4@ CeO2 nanofibers
CN109433241A (en) A kind of quantum-dot modified TiO of carbonitride2The preparation and application of photonic crystal catalyst
CN114192146B (en) Magnetic microporous carbon-based cobalt catalyst based on space confinement effect and preparation method and application thereof
CN107892354A (en) A kind of device and method of photocatalytic degradation of dye waste water
CN108654586A (en) A kind of graphitization mesoporous carbon-TiO2Composite photocatalyst material and the preparation method and application thereof
CN112495415A (en) Nanotube catalytic material and preparation method and application thereof
Bai et al. Study on the controlled synthesis of Zr/TiO2/SBA-15 nanophotocatalyst and its photocatalytic performance for industrial dye reactive red X–3B
Wang et al. Upconversion Tm3+: CeO2/palygorskite as direct Z-scheme heterostructure for photocatalytic degradation of bisphenol A
Li et al. Synthesis of hierarchically porous Cu–Ni/C composite catalysts from tissue paper and their catalytic activity for the degradation of triphenylmethane dye in the microwave induced catalytic oxidation (MICO) process
CN108452788A (en) The preparation method and application of interstitial boron doped titanium dioxide photocatalytic material
CN105883910B (en) A kind of perovskite SrTiO3The preparation method and product of porous nano particle
Li et al. Unique kinetics feature and excellent photocatalytic performance of tetracycline photodegradation using yolk-shell TiO2@ void@ TiO2: Eu3+
Cheng et al. Visible-light-driven hierarchical porous CeO2 derived from wood for effective photocatalytic degradation of methylene blue

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20230801

Address after: 215532 Bosideng Industrial Park, Guli Town, Changshu City, Suzhou City, Jiangsu Province

Patentee after: BOSIDENG DOWN WEAR Co.,Ltd.

Address before: No. 1800, Lihu Avenue, Binhu District, Wuxi City, Jiangsu Province

Patentee before: Jiangnan University