CN107986380A - A kind of N doping coateds TiO2The technique of photocatalyst for degrading waste water - Google Patents

A kind of N doping coateds TiO2The technique of photocatalyst for degrading waste water Download PDF

Info

Publication number
CN107986380A
CN107986380A CN201711253833.9A CN201711253833A CN107986380A CN 107986380 A CN107986380 A CN 107986380A CN 201711253833 A CN201711253833 A CN 201711253833A CN 107986380 A CN107986380 A CN 107986380A
Authority
CN
China
Prior art keywords
tio
room temperature
powder
encapsulated type
dyestuff
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
CN201711253833.9A
Other languages
Chinese (zh)
Other versions
CN107986380B (en
Inventor
延海平
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.)
Boxing Ruifeng New Material Co ltd
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CN201711253833.9A priority Critical patent/CN107986380B/en
Publication of CN107986380A publication Critical patent/CN107986380A/en
Application granted granted Critical
Publication of CN107986380B publication Critical patent/CN107986380B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • 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
    • B01J27/24Nitrogen compounds
    • B01J35/39
    • 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
    • C02F2101/36Organic 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
    • C02F2305/10Photocatalysts

Abstract

The invention discloses a kind for the treatment of process of photocatalytic degradation of dye waste water, unordered nano-encapsulated type TiO that its visible light catalyst used adulterates for N2Photochemical catalyst.The unordered nano-encapsulated type TiO with thin multi-layer core-shell structure is made in the catalyst first2, then N is mixed in original position in its lattice, and the doping of the specificity and N element of structure improves TiO jointly2To the Photocatalytic activity of organic dyestuff.The present invention solves the problems, such as that dye wastewater degradation efficiency is low in the prior art, the organic dyestuff suitable for pollution degradation water body.

Description

A kind of N doping coateds TiO2The technique of photocatalyst for degrading waste water
Technical field
The present invention relates to a kind for the treatment of process of photocatalytic degradation of dye waste water, the unordered nano-encapsulated type adulterated using N TiO2Photochemical catalyst, the special structure of the photochemical catalyst and N element are in TiO2Doping between lattice has been obviously improved TiO2Photocatalysis The visible light catalysis activity of agent, the treatment process have the advantages that easy to operate, of low cost, degradation efficiency is high.
Background technology
In textile printing and dyeing process, largely use pollution environment and harmful auxiliary agent, these auxiliary agents big Discharged more in the form of liquid, inevitably into water body environment, cause water pollution.If rhdamine B is with carcinogenic And mutagenicity, the chroma in waste water containing rhodamine B is deep, organic pollution content is high, biological degradability is poor, with conventional method Such as physisorphtion, Fenton process are difficult to administer, and cause to pollute water quality long-term degradation, seriously endanger the strong of water body environment and the mankind Health, therefore seem particularly significant and urgent to the degradation treatment of this kind of waste water.
But how to use clean energy resource high efficiency, low cost, it is still one and huge challenge and there is far-reaching meaning Justice.So there is an urgent need to develop new energy such as solar energy, wind energy, tide energy, biological energy source, the hydrogen using environmentally friendly and high energy storage by people Energy, ocean energy etc., can cost-effectively substitute fossil and mineral resources, real on the premise of environmental protection and human health Effectively converting and not influencing people for the existing energy is normally lived.A large amount of Novel environment-friendlymaterial materials are come into being in recent years.Nanometer TiO2Material be exactly it is this can environment purification and efficiently utilize solar energy green functional material.It not only has oxidability By force, excellent chemical stability, energy expenditure, without follow-up secondary pollution the advantages that, but also there is cheap, nontoxic nothing Evil, can long-time service the features such as, therefore enjoy the favor and concern of photocatalysis researcher in recent years, and it extensively should For the quick magnificent solar cell of new energy field such as dyestuff, photodissociation aquatic products hydrogen, microwave absorption, light absorption, biological medicine processing, light Lie prostrate battery, photocatalysis, lithium ion battery etc..
But semiconductor TiO2Material there is also some it is serious the defects of, such as pure TiO2The photo-generate electron-hole of photochemical catalyst To short life, light abstraction width is narrow low with light conversion efficiency, limits the application of solid powder th-1 catalyst.So need to receiving The pattern of rice titanium dioxide is modified and study on the modification, and it is extremely urgent to sun efficiency of light absorption to improve it.Therefore, close Reason ground prepares Hydrogen Energy with solar energy and conductor oxidate and effectively Environment control will be subject to people more and more to pay attention to.
From solar-energy photo-voltaic cell under the conditions of Japanese Scientists Fujishima and Honda discovery ultraviolet light in 1972 TiO2During electrode there occurs the interesting fact of photocatalytic water since, since nearly half a century, researchers are put into largely Energy research TiO2Modification, illustrate analyze its catalytic mechanism, with deepening continuously for research, light-catalyzed reaction mechanism is further It is clear, on TiO2The fast rapid-result focus of research, and also achieve different degrees of progress in all fields, but from The theoretical research stage in laboratory is still on the whole, also has very big distance apart from industrial applications, in order to effectively improve TiO2The catalytic activity of catalyst, currently used method include that narrow gap semiconductor is compound therewith, metal and nonmetal ion Doping, noble metal loading, surface photosensitizer the methods of come change catalytic inner crystalline structure and outside surface group Into and property reduce catalyst band gap distance, improve catalyst to the absorbability of visible ray reach enhancing TiO2Photocatalytic The purpose of energy.
In recent years, Mao etc. employs a kind of breakthrough method for hydrogenation and is prepared for a unordered nano-TiO2, thus method The TiO being prepared into2Energy gap there was only 1.54eV, possess very outstanding visible absorption performance and photolysis water hydrogen Performance, but modification is doped to it, and use it for the organic pollution in photocatalyst for degrading water body and relevant degraded Then there has been no systematic research for technique.
The content of the invention
The shortcomings that in order to overcome the above-mentioned prior art, it is an object of the invention to provide a kind of photocatalytic degradation of dye waste water Treatment process, it uses light-catalysed mode to degrade dyestuff therein, and used photochemical catalyst is the unordered nanometer of N doping Coated TiO2
Realize technical scheme:Waste water from dyestuff is handled by the way of a kind of Visible Light Induced Photocatalytic, and is prepared for one The unordered nano-encapsulated type TiO that N of the kind with excellent Photocatalytic activity is adulterated2Photochemical catalyst.
The treatment process of the Visible Light Induced Photocatalytic waste water from dyestuff, includes the following steps:
The unordered nano-encapsulated type TiO that N is adulterated2Photochemical catalyst is added to concentration as in 8mg/L~25mg/L waste water from dyestuff, Room temperature, stirring visible light catalytic 0.5~3h of reaction are carried out under the xenon lamp of 400W~600W, the photochemical catalyst and waste water from dyestuff Ratio is 35~45g:100L, the liquid level distance of xenon lamp and the waste water from dyestuff is 18cm~22cm, when one section of illumination reaction Between after, close xenon lamp, complete the degraded to dyestuff.The dyestuff is at least one in methyl orange, methylene blue, rhodamine B Kind.
The unordered nano-encapsulated type TiO of N doping2Preparation method, be specifically realized by the following steps:
First, unordered nano-encapsulated type TiO2Preparation:
A, by TiO2And NaBH4Mixing, grinds 0.5~1h, obtains mixture, the TiO2With NaBH4Mass ratio be 1:(0.6 ~0.7);
B, the mixture for obtaining step a is moved into alumina crucible, then is placed in tube furnace, with 10 DEG C/min under nitrogen atmosphere The speed of~20 DEG C/min maintains 0.5~1h, then furnace cooling under this condition from room temperature to 300 DEG C~400 DEG C To room temperature, the powder after being reacted;
C, the powder obtained step b is moved into alumina crucible, then is placed in tube furnace, under argon gas atmosphere with 10 DEG C/min~ The speed of 20 DEG C/min maintains 0.5~1h under this condition from room temperature to 300 DEG C~400 DEG C, then cools to the furnace Room temperature, and with repeatedly washing and the drying of second alcohol and water, the powder after being reacted;
D, the powder for obtaining step c again with NaBH4Mixing, grinds 1~2h, obtains mixture, the powder that the step c is obtained End and NaBH4Mass ratio be 1:(0.8~0.9);
E, the mixture for obtaining step d is moved into alumina crucible, then is placed in tube furnace, with 2 DEG C/min under argon gas atmosphere The speed of~5 DEG C/min maintains 0.5~1h under this condition from room temperature to 300 DEG C~400 DEG C, then furnace cooling, Powder after being reacted;
F, the powder after reaction is washed 2~5 times respectively successively with ethanol and deionized water, is finally carried out in air dry oven It is dry, obtain TiO2Powder;
G, the TiO for obtaining step f2Powder is moved into alumina crucible, then is placed in tube furnace, in air atmosphere with 2 DEG C/ The speed of min~5 DEG C/min handles 0.5~2h under this condition from room temperature to 300 DEG C~500 DEG C, then with furnace cooling But to room temperature, unordered nano-encapsulated type TiO is obtained2
The unordered nano-encapsulated type TiO2With multi-layer core-shell structure, TiO is followed successively by from inside to outside2Crystal nuclear, reduction amorphous Layer, oxidation crystal layer, reduction amorphous layer, oxidation crystal layer, thickness is gradually thinning and is in close contact, the thin multi-layer core-shell structure Enhance the quick conduction of light induced electron and its separation with hole.
2nd, the unordered nano-encapsulated type TiO of N doping2Preparation:
By unordered nano-encapsulated type TiO made from a certain amount of step 12It is uniformly mixed, is placed in full of inert atmosphere with urea In tube furnace, with the speed of 2 DEG C/min~5 DEG C/min from room temperature to 400 DEG C~500 DEG C, and 2h is maintained, then with furnace cooling But to room temperature, the unordered nano-encapsulated type TiO of N doping is obtained2, wherein unordered nano-encapsulated type TiO2Mass ratio with urea is 1:(0.3~0.5).
Rhodamine B(Rhodamine B, RhB)Safflower powder generally is called, a length of 553.2nmn of its maximum absorption wave.Luo Dan Bright B dyestuffs are initially used to the organic dyestuff as oxa anthracenes, this dyestuff has certain causing toxicity, its suction in aqueous Luminosity is stronger, and smaller, test process simple and convenient is influenced by external condition, therefore selects RhB as target contaminant to simulate Assess the catalytic efficiency of catalysis material.
Specific test method is as follows:The RhB solution 100mL of 10mg/L is prepared as reaction contaminant, adds suitable N The unordered nano-encapsulated type TiO of doping2, it is placed on the progress ultrasonic disperse regular hour in ultrasonic cleaning machine.Then by the solution It is put into camera bellows, under the irradiation such as xenon lamp of filtering ultraviolet light, investigates the degrading activity of different time catalyst.
Compared with prior art, the present invention has the following advantages:
1st, compared with prior art, processing method of the invention is easy to operate, easy control of reaction conditions, of low cost, has Potential industrial applications prospect;
2nd, photochemical catalyst of the present invention to prepare reaction condition gentle, it is easy to operate, it is dangerous small.Prepared with simple annealing steps Possesses the TiO of multi-layer core-shell structure2, the TiO of this special multi-layer core-shell structure2Photochemical catalyst more effectively inhibits photoproduction Electronics and hole it is compound, extend the service life in electronics and hole, increase electron concentration, make it as photochemical catalyst for degrading Activity during dyestuff is significantly improved;
3rd, the doping of N enables N element to enter TiO2Lattice in, cause distortion of lattice, N element improves TiO2Catalyst Ratio surface, it can improve light absorpting ability of the catalyst to visible ray, so as to improve the visible light catalytic efficiency of material.
Embodiment
With reference to specific embodiment the present invention is further elaborated the solution of the present invention.
Embodiment 1
First, unordered nano-encapsulated type TiO2Preparation:
A, by TiO2And NaBH4Mixing, grinds 0.5h, obtains mixture, the TiO2With NaBH4Mass ratio be 1:0.65;
B, the mixture for obtaining step a is moved into alumina crucible, then is placed in tube furnace, with 10 DEG C/min under nitrogen atmosphere Speed from room temperature to 350 DEG C, and maintain 0.5h under this condition, room temperature then cooled to the furnace, after being reacted Powder;
C, the powder for obtaining step b is moved into alumina crucible, then is placed in tube furnace, with 10 DEG C/min's under argon gas atmosphere Speed maintains 0.5h under this condition from room temperature to 400 DEG C, then cools to room temperature with the furnace, and more with second alcohol and water Secondary washing and drying, the powders A after being reacted;
D, the powders A for obtaining step c again with NaBH4Mixing, grinds 1.5h, obtains mixture, the powder that the step c is obtained Last A and NaBH4Mass ratio be 1:0.85;
E, the mixture for obtaining step d is moved into alumina crucible, then is placed in tube furnace, with 2 DEG C/min under argon gas atmosphere Speed from room temperature to 400 DEG C, and maintain 0.5h under this condition, then furnace cooling, the powder after being reacted;
F, the powder after reaction is washed 2~5 times respectively successively with ethanol and deionized water, is finally carried out in air dry oven It is dry, obtain TiO2Powder;
G, the TiO for obtaining step f2Powder is moved into alumina crucible, then is placed in tube furnace, in air atmosphere with 2 DEG C/ The speed of min~5 DEG C/min handles 0.5~2h under this condition from room temperature to 300 DEG C~500 DEG C, then with furnace cooling But to room temperature, unordered nano-encapsulated type TiO is obtained2Powder B.
2nd, the unordered nano-encapsulated type TiO of N doping2Preparation:
By obtained unordered nano-encapsulated type TiO in a certain amount of step 12Powder B is uniformly mixed with urea, is placed in full of lazy In the tube furnace of property atmosphere, with the speed of 2 DEG C/min from room temperature to 400 DEG C, and 2h is maintained, then cool to room with the furnace Temperature, obtains the unordered nano-encapsulated type TiO of N doping2, wherein powders A or unordered nano-encapsulated type TiO2Mass ratio with urea is 1:(0.3~0.5).
The treatment process of RhB waste water is as follows:The RhB solution 100mL of three parts of 10mg/L is prepared as reaction contaminant, difference Add obtained undoped powders A in equivalent embodiment 1, the unordered nano-encapsulated type of undoped powder B and N doping TiO2, it is placed in ultrasonic cleaning machine and carries out ultrasonic disperse 0.5h.Then the solution is put into 30min in camera bellows, keep xenon lamp with The liquid level distance of waste water from dyestuff is 20cm, then under the xenon lamp irradiation of filtering ultraviolet light, every in 30min sampling analysis sample liquids The concentration of RhB, so as to investigate the degrading activity of different time catalyst, specific data are referring to table 1 below:
The photocatalytic activity test of the different samples of table 1.
From the data analysis in table 1, once reduced, for the powders A of oxidation processes compared to only passing through, by going back twice Former, the unordered nano-encapsulated type TiO of oxidation processes2Photocatalytic degradation RhB activity it is clearly more powerful, this is because locating twice Introduced after reason gradually thin multi-layer core-shell structure enhances the quick conduction of light induced electron and its separation with hole from inside to outside, from And enhance TiO2Photocatalytic activity.In addition, again it can be seen that the doping of N element equally can be carried significantly from upper table Rise unordered nano-encapsulated type TiO2Photocatalytic activity.It can be seen from the above that the unordered nanometer bag that N made from the solution of the present invention is adulterated Wrap up in type TiO2With excellent photocatalyst for degrading effect.
The foregoing is only a preferred embodiment of the present invention, but protection scope of the present invention be not limited thereto, Any one skilled in the art the invention discloses technical scope in, technique according to the invention scheme and its Inventive concept is subject to equivalent substitution or change, should be covered by the protection scope of the present invention.

Claims (5)

1. a kind for the treatment of process of Visible Light Induced Photocatalytic waste water from dyestuff, includes the following steps:
The unordered nano-encapsulated type TiO that N is adulterated2Photochemical catalyst is added to concentration as in 8mg/L~25mg/L waste water from dyestuff, Room temperature, stirring visible light catalytic 0.5~3h of reaction are carried out under the xenon lamp of 400W~600W, the photochemical catalyst and waste water from dyestuff Ratio is 35~45g:100L, the liquid level distance of xenon lamp and the waste water from dyestuff is 18cm~22cm, when one section of illumination reaction Between after, close xenon lamp, complete the degraded to dyestuff.
2. treatment process as claimed in claim 1, the dyestuff is at least one in methyl orange, methylene blue, rhodamine B Kind.
3. treatment process as claimed in claim 1, it is characterised in that the unordered nano-encapsulated type TiO of the N doping2It can be seen that The preparation method of photochemical catalyst is first to prepare the unordered nano-encapsulated type TiO with thin multi-layer core-shell structure2, then in TiO2It is brilliant N element is adulterated in lattice to be made.
4. treatment process according to claim 3, it is characterised in that the unordered nano-encapsulated of the thin multi-layer core-shell structure Type TiO2Preparation method it is as follows:
A, by TiO2And NaBH4Mixing, grinds 0.5~1h, obtains mixture, the TiO2With NaBH4Mass ratio be 1:(0.6 ~0.7);
B, the mixture for obtaining step a is moved into alumina crucible, then is placed in tube furnace, with 10 DEG C/min under nitrogen atmosphere The speed of~20 DEG C/min maintains 0.5~1h, then furnace cooling under this condition from room temperature to 300 DEG C~400 DEG C To room temperature, the powder after being reacted;
C, the powder obtained step b is moved into alumina crucible, then is placed in tube furnace, under argon gas atmosphere with 10 DEG C/min~ The speed of 20 DEG C/min maintains 0.5~1h under this condition from room temperature to 300 DEG C~400 DEG C, then cools to the furnace Room temperature, and with repeatedly washing and the drying of second alcohol and water, the powder after being reacted;
D, the powder for obtaining step c again with NaBH4Mixing, grinds 1~2h, obtains mixture, the powder that the step c is obtained End and NaBH4Mass ratio be 1:(0.8~0.9);
E, the mixture for obtaining step d is moved into alumina crucible, then is placed in tube furnace, with 2 DEG C/min under argon gas atmosphere The speed of~5 DEG C/min maintains 0.5~1h under this condition from room temperature to 300 DEG C~400 DEG C, then furnace cooling, Powder after being reacted;
F, the powder after reaction is washed 2~5 times respectively successively with ethanol and deionized water, is finally carried out in air dry oven It is dry, obtain TiO2Powder;
G, the TiO for obtaining step f2Powder is moved into alumina crucible, then is placed in tube furnace, in air atmosphere with 2 DEG C/ The speed of min~5 DEG C/min handles 0.5~2h under this condition from room temperature to 300 DEG C~500 DEG C, then with furnace cooling But to room temperature, unordered nano-encapsulated type TiO is obtained2
5. according to 3 or 4 any one of them treatment process of claim, it is characterised in that described in TiO2N members are adulterated in lattice The method of element is as follows:By unordered nano-encapsulated type TiO made from a certain amount of step 12It is uniformly mixed with urea, is placed in being full of In the tube furnace of inert atmosphere, with the speed of 2 DEG C/min~5 DEG C/min from room temperature to 400 DEG C~500 DEG C, and 2h is maintained, Then cool to room temperature with the furnace, obtain the unordered nano-encapsulated type TiO of N doping2, wherein unordered nano-encapsulated type TiO2With urea Mass ratio be 1:(0.3~0.5).
CN201711253833.9A 2017-12-02 2017-12-02 N-doped wrapped TiO2Process for degrading wastewater by using photocatalyst Active CN107986380B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201711253833.9A CN107986380B (en) 2017-12-02 2017-12-02 N-doped wrapped TiO2Process for degrading wastewater by using photocatalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201711253833.9A CN107986380B (en) 2017-12-02 2017-12-02 N-doped wrapped TiO2Process for degrading wastewater by using photocatalyst

Publications (2)

Publication Number Publication Date
CN107986380A true CN107986380A (en) 2018-05-04
CN107986380B CN107986380B (en) 2021-08-27

Family

ID=62035327

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201711253833.9A Active CN107986380B (en) 2017-12-02 2017-12-02 N-doped wrapped TiO2Process for degrading wastewater by using photocatalyst

Country Status (1)

Country Link
CN (1) CN107986380B (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108607597A (en) * 2018-05-24 2018-10-02 青岛理工大学 A kind of method of photo catalytic reduction Cr (VI) under visible light
CN110280284A (en) * 2019-06-09 2019-09-27 浙江理工大学 A kind of synchronous preparation C3N4And TiOxN2-xThe method of visible light catalyst
CN112117020A (en) * 2020-09-09 2020-12-22 中国工程物理研究院核物理与化学研究所 Method for treating tritium water by photo-thermal concerted catalysis
CN114247458A (en) * 2020-09-23 2022-03-29 国家能源投资集团有限责任公司 Preparation method and application of nitrogen-doped titanium dioxide denitration catalyst
CN117483010A (en) * 2024-01-03 2024-02-02 山东海化集团有限公司 Modified nano TiO 2 Preparation method and application of catalyst

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003287601A (en) * 2002-03-27 2003-10-10 Murakami Corp Composite material
CN101013620A (en) * 2006-12-14 2007-08-08 复旦大学 Magnetic nanometer particle with triple core-shell structure and method for making same
CN101259422A (en) * 2008-04-24 2008-09-10 南开大学 Preparation of high efficiency nano Ti1-XO2-SnX/TiO2-X-NX compound film
US20140060643A1 (en) * 2012-09-05 2014-03-06 Lane W. Martin Light Absorbing Oxide Materials for Photovoltaic and Photocatalytic Applications and Devices
CN105327717A (en) * 2015-12-03 2016-02-17 湖南科技大学 Nano-gold cyclohexane oxidation catalyst encapsulated through SiO2 and mesoporous TiO2 hollow microspheres and preparation and application of nano-gold cyclohexane oxidation catalyst
CN105771948A (en) * 2016-04-08 2016-07-20 哈尔滨师范大学 Double-shell titanium dioxide catalyst with high photocatalytic hydrogen generation performance and preparation method thereof
CN105858722A (en) * 2016-06-14 2016-08-17 福建中烟工业有限责任公司 Preparation method of N-doped TiO2
CN106082317A (en) * 2016-05-31 2016-11-09 陕西科技大学 A kind of preparation method of hollow hemisphere titanium dioxide
CN106856241A (en) * 2016-12-29 2017-06-16 南京邮电大学 A kind of multiphase composite nanostructure negative material and preparation method thereof
CN107185595A (en) * 2017-05-31 2017-09-22 北京三聚环保新材料股份有限公司 One kind is with TiO2For the preparation method of the hud typed carrier of shell
CN107376975A (en) * 2017-08-17 2017-11-24 中国科学院生态环境研究中心 Visible light catalysis activity N doping nucleocapsid shape titanium dioxide and preparation method thereof

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003287601A (en) * 2002-03-27 2003-10-10 Murakami Corp Composite material
CN101013620A (en) * 2006-12-14 2007-08-08 复旦大学 Magnetic nanometer particle with triple core-shell structure and method for making same
CN101259422A (en) * 2008-04-24 2008-09-10 南开大学 Preparation of high efficiency nano Ti1-XO2-SnX/TiO2-X-NX compound film
US20140060643A1 (en) * 2012-09-05 2014-03-06 Lane W. Martin Light Absorbing Oxide Materials for Photovoltaic and Photocatalytic Applications and Devices
CN105327717A (en) * 2015-12-03 2016-02-17 湖南科技大学 Nano-gold cyclohexane oxidation catalyst encapsulated through SiO2 and mesoporous TiO2 hollow microspheres and preparation and application of nano-gold cyclohexane oxidation catalyst
CN105771948A (en) * 2016-04-08 2016-07-20 哈尔滨师范大学 Double-shell titanium dioxide catalyst with high photocatalytic hydrogen generation performance and preparation method thereof
CN106082317A (en) * 2016-05-31 2016-11-09 陕西科技大学 A kind of preparation method of hollow hemisphere titanium dioxide
CN105858722A (en) * 2016-06-14 2016-08-17 福建中烟工业有限责任公司 Preparation method of N-doped TiO2
CN106856241A (en) * 2016-12-29 2017-06-16 南京邮电大学 A kind of multiphase composite nanostructure negative material and preparation method thereof
CN107185595A (en) * 2017-05-31 2017-09-22 北京三聚环保新材料股份有限公司 One kind is with TiO2For the preparation method of the hud typed carrier of shell
CN107376975A (en) * 2017-08-17 2017-11-24 中国科学院生态环境研究中心 Visible light catalysis activity N doping nucleocapsid shape titanium dioxide and preparation method thereof

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
ZHANG WEN-GANG等: "Research on Photoeatalytic Performance Influencing Factors of Asphalt Mixture Adulterated with TiO2", 《JOURNAL OF WUHAN UNIVERSITY OF TECHNOLOGY》 *
张祖云等: "石墨棒载Bi_xTiO_y-TiO_2复合膜电极光电催化降解亚甲蓝 ", 《南京师大学报(自然科学版)》 *
赵宏生等: "氮掺杂二氧化钛薄膜的制备与光催化性能 ", 《稀有金属材料与工程》 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108607597A (en) * 2018-05-24 2018-10-02 青岛理工大学 A kind of method of photo catalytic reduction Cr (VI) under visible light
CN110280284A (en) * 2019-06-09 2019-09-27 浙江理工大学 A kind of synchronous preparation C3N4And TiOxN2-xThe method of visible light catalyst
CN110280284B (en) * 2019-06-09 2022-03-25 浙江理工大学 Synchronous preparation of C3N4And TiOxN2-xMethod for visible light catalyst
CN112117020A (en) * 2020-09-09 2020-12-22 中国工程物理研究院核物理与化学研究所 Method for treating tritium water by photo-thermal concerted catalysis
CN114247458A (en) * 2020-09-23 2022-03-29 国家能源投资集团有限责任公司 Preparation method and application of nitrogen-doped titanium dioxide denitration catalyst
CN114247458B (en) * 2020-09-23 2024-02-13 国家能源投资集团有限责任公司 Preparation method and application of nitrogen-doped titanium dioxide denitration catalyst
CN117483010A (en) * 2024-01-03 2024-02-02 山东海化集团有限公司 Modified nano TiO 2 Preparation method and application of catalyst

Also Published As

Publication number Publication date
CN107986380B (en) 2021-08-27

Similar Documents

Publication Publication Date Title
CN107986380A (en) A kind of N doping coateds TiO2The technique of photocatalyst for degrading waste water
Guo et al. Mesocrystalline Ta3N5 superstructures with long-lived charges for improved visible light photocatalytic hydrogen production
CN105664979B (en) A kind of mesoporous nano microspheroidal Ln-Bi5O7I photochemical catalysts and preparation method thereof
Zhong et al. Preparation of a novel composite photocatalyst BiOBr/ZIF-67 for enhanced visible-light photocatalytic degradation of RhB
CN109675607A (en) Fe3O4The preparation method of@ZnO@N-C composite photocatalyst material
CN111068715B (en) Ag/Bi 2 O 3 /CuBi 2 O 4 Preparation method of nanofiber composite photocatalyst
CN109225273B (en) Copper sulfide/tungsten sulfide composite photocatalyst and preparation method thereof
CN106944074A (en) A kind of visible-light response type composite photo-catalyst and its preparation method and application
CN109847780A (en) A kind of AgBr/BiOI/g-C3N4The preparation method and applications of tri compound catalysis material
CN107935103A (en) A kind for the treatment of process of silver-based composite photocatalyst for degrading dyeing waste water
Feng et al. Effective H2O2-Free photo-Fenton processes over ZnSe nanosheets for photocatalytic degradation of dyes and antibiotics
CN108654671B (en) Composite photocatalyst and preparation method and application thereof
CN111530490A (en) Co3O4-TiO2Heterojunction loaded carbon nanotube photocatalytic degradation material and preparation method thereof
CN112495399A (en) MoS2Nano flower-Ag doped porous BiVO4Preparation method of photocatalytic degradation material
CN114247452A (en) Bismuth-bismuth sulfide-bismuth tungstate composite photocatalyst and preparation method and application thereof
Xie et al. Evaluation of visible photocatalytic performance of microwave hydrothermal synthesis of MnO2/TiO2 core-shell structures and gaseous mercury removal
CN108144599A (en) A kind for the treatment of process of bismuthino composite photocatalyst for degrading dyeing waste water
Yuan et al. A high-efficiency solar water evaporation-photocatalysis system achieved by manipulating surface wettability and constructing heterojunction
Shen et al. Unravelling the favorable photocatalytic effect of hydrogenation process on the novel g-C3N4-TiO2 catalysts for water purification
CN106111179B (en) A kind of small size nitrogen-doped graphene photochemical catalyst and its preparation method and application
CN107973367A (en) A kind of Fe doping coateds TiO2The technique of photocatalyst for degrading waste water
CN103866314B (en) The preparation method and application of visible light-responded black titanium dioxide nano thin-film
CN108117130A (en) A kind for the treatment of process of auri composite photocatalyst for degrading dyeing waste water
CN112495400A (en) SnS with S vacancy2Preparation of nanosheet and application thereof in photodegradation of Cr (VI)
CN107029719A (en) A kind of Bi2O3/Ag2WO4/Bi2WO6Composite photo-catalyst and preparation method and application

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
TA01 Transfer of patent application right

Effective date of registration: 20210809

Address after: 325600 room 402, building g, Lane 111, Mingyang Road, Lecheng street, Yueqing City, Wenzhou City, Zhejiang Province

Applicant after: Huang Jianyong

Address before: 251800 Xingfu 1st Road, Yangxin County, Binzhou City, Shandong Province

Applicant before: Yanhaiping

TA01 Transfer of patent application right
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20230214

Address after: No. 419, Central Road, Xizha Village, Jinqiu Sub district Office, Boxing Economic Development Zone, Boxing County, Binzhou City, Shandong Province, 256500

Patentee after: Boxing Ruifeng New Material Co.,Ltd.

Address before: 325600 room 402, building g, Lane 111, Mingyang Road, Lecheng street, Yueqing City, Wenzhou City, Zhejiang Province

Patentee before: Huang Jianyong

TR01 Transfer of patent right