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CN107376891A - Double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing - Google Patents

Double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing Download PDF

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Publication number
CN107376891A
CN107376891A CN201710640852.0A CN201710640852A CN107376891A CN 107376891 A CN107376891 A CN 107376891A CN 201710640852 A CN201710640852 A CN 201710640852A CN 107376891 A CN107376891 A CN 107376891A
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rare earth
nitrate
titanium oxide
preparation methods
oxide catalyst
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CN201710640852.0A
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Inventor
何丹农
林琳
徐少洪
王艳丽
金彩虹
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Shanghai National Engineering Research Center for Nanotechnology Co Ltd
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Shanghai National Engineering Research Center for Nanotechnology Co Ltd
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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
    • 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
    • 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
    • B01J23/10Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of rare earths
    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts
    • 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

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

Abstract

The present invention relates to a kind of double rare earth codoping titanium oxide catalyst preparation methods with visible light activity of tetracycline wastewater processing, urea, rare earth element nitrate, CTAB are added in ethylene glycol and dissolved, liquid phase titanium source is added in above-mentioned solution afterwards, forms homogeneous phase solution.Then deionized water is added while stirring, forms clear gel.Above-mentioned gel is subjected to hydro-thermal process, washing, filtering and drying, obtains double rare-earth elements doped titanium dioxide photocatalyst afterwards.The voluntarily regulation and control that acid-base value is carried out to reaction system are slowly decomposed by urea in water-heat process, realize purpose of the rare earth element to titanium dioxide codope.The preparation method simple process, Parameter adjustable scope is wide, and repeatability is strong, and cost is low, and obtained titanium dioxide optical catalyst has preferable degradation effect under visible light conditions to tetracycline wastewater.

Description

Double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing
Technical field
The present invention relates to a kind of double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing, and pass through The product and application that the preparation method obtains.The preparation method can widen the visible light-responded scope of titanium dioxide optical catalyst.
Background technology
With the continuous development of pharmaceuticals industry, China turns into the big production of raw medicine state of the first in the world, due to production technology And the reason for technology, in antibiotics production there is raw material availability it is low, refine that purity is low, residual fungistatic cellulose content is high in waste water The problems such as, up to 50,000,000 tons of wastewater flow rate causing domestic 300 Duo Jia antibiotics productions enterprises to discharge every year.Antibiotic waste water Discharge causes large effect to ecological environment, and being continuously increased of the usage amount of particularly current antibiotic is caused bigger to environment Influence.Antibiotic is that human treatment's infectious diseases brings huge convenience, has effectively ensured the health of the mankind, but simultaneously by In the abuse of antibiotic, animal husbandry, culture fishery etc. largely use antibiotic in addition, make antibiotic residual in the environment and Its caused resistance problems is on the rise, and the negative effect that the mankind and ecological environment bring increasingly is strengthened, threatened The health of the mankind.Such as hereditary variation, the resistance to the action of a drug, double infection, toxicity, allergic reaction, particularly because the resistance to the action of a drug triggers Superbacteria occurs, and causes global concern.Therefore, the medical antibiotic contamination in water body environment is removed by ring Border worker is considered as an important goal in research, how effectively to handle antibiotic residue waste water for improving pharmacy waste water water outlet The water quality even overall water quality of China is all significant.
For titanium dioxide because chemical property is stable, heat endurance is high, and catalytic activity is high, and anti-light corrosion, nontoxic, raw material is easy to get The advantages that show one's talent in numerous conductor oxidates, be widely used in air, the degraded of water environment pollution thing, antibacterial, remove The fields such as smelly and automatically cleaning.But titanium dioxide is as photochemical catalyst that there is also two large problems:First, energy gap causes greatly two Titanium oxide is extremely low to the utilization rate of sunshine.At normal temperatures, during pH=1, the energy gap of the titanium dioxide of Detitanium-ore-type is about 3.2eV, according to Einstein equation, it can only absorbing wavelength be less than 375nm ultraviolet light, and this part ultraviolet light accounts for sunshine Gross energy less than 5%.This results in titanium dioxide can not make full use of to being radiated tellurian sunshine, greatly limitation The use range of catalyst;Secondly, the quantum efficiency of titanium dioxide optical catalyst is too low, light activated electronics and hole life It is short, it is easily compound, cause most photoproduction load to carry out effective light-catalyzed reaction, this is also to hinder photocatalytic activity The big limiting factor further improved, the two factors significantly limit its use in actual production and life.
In recent years, people are attempted by metal-doped, nonmetal doping, metal and nonmetallic codope, semiconductors coupling With the means such as dye photoactivation, the photoresponse scope of titanium dioxide is expanded, suppresses the compound of electronics and hole, so as to improve dioxy Change the photocatalysis performance of titanium and its compound.
The content of the invention
For overcome the deficiencies in the prior art, present invention aims at provide a kind of double rare earths of tetracycline wastewater processing to be co-doped with Miscellaneous titanium deoxide catalyst preparation method.
Another object of the present invention is:The product that above-mentioned preparation method obtains is provided.
A further object of the present invention is:The application of the said goods is provided.
The object of the invention is realized by following proposal:
A kind of double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing, with titanate esters, cetyl front three Base ammonium bromide(CTAB), water, ethylene glycol, urea, rare earth nitrades be raw material, wherein, described titanate esters are liquid phase titanium source, bag Include following steps:
(1)Urea, CTAB, two kinds of rare earth nitrades are added in ethylene glycol, liquid phase titanium source is added after stirring and dissolving, stirring is formed Homogeneous phase solution, deionized water is then added dropwise while stirring in above-mentioned system, until formed clear gel, titanate esters and two kinds it is dilute The mol ratio of native nitrate is 1:0.025:0.025~1:0.15:0.15;
(2)Above-mentioned gel is put into the stainless steel autoclave of teflon lined, at 150 ~ 200 DEG C hydro-thermal reaction 8 ~ Precipitated product is washed with deionized after terminating for 24h, reaction, until the pH of cleaning solution is in neutrality, the then drying at 80 DEG C More than 10h, processing is dried, dry sample is calcined 2h at 400 DEG C, it is double dilute that removing residual organic matter obtains object Native codope titanium dioxide composite nano materials.
In the present invention, liquid phase titanium source slowly hydrolyzes to form aqua oxidation titanium gel, and rare earth ion is evenly dispersed in water Close in titanium oxide gel;By slow decomposition of the urea in hydrothermal reaction process, the acid-base property of system is gradually to alkalescent side To movement, in situ doping of the thulium in titanium oxide lattice is realized.The preparation method technique and simple flow, ginseng Number adjustable extent is wide, and repeatability is strong, and cost is low.Slowly decomposed by urea in water-heat process and acid-base value is carried out to reaction system Voluntarily regulation and control, realize purpose of the rare earth element to titanium dioxide codope.The preparation method technique and simple flow, parameter can Adjust scope wide, repeatability is strong, and cost is low, and the titanium dioxide optical catalyst of preparation has under visible light conditions to tetracycline wastewater There is preferable degradation effect.
Described rare earth nitrades are hydration or non-hydrated cerous nitrate, lanthanum nitrate, neodymium nitrate, yttrium nitrate, gadolinium nitrate, nitre Any two kinds in sour europium, terbium nitrate, samaric nitrate, thulium nitrate, erbium nitrate, ytterbium nitrate.
Titanate esters, CTAB, water, the mol ratio of ethylene glycol and urea are 1:0.5~1:1000~2000:1000~2000: 20~40.
On the basis of such scheme, described liquid phase titanium source refers to:Tetra-n-butyl titanate, isopropyl titanate, metatitanic acid tetrem The mixture of liquid phase titanium source more than one or both of ester.
The molar ratio of two kinds of rare earth elements is 1:1.
Present invention process is simple, the double rare earth codoped titanium dioxide visible light catalysts obtained by above-mentioned preparation method, carries High titanium dioxide specific surface area, widens its visible light-responded scope.
There is following mechanism after double rare earth codopes:(a) trap center is formed, valence state is higher than Ti4+Metal ion capture Electronics, the metal ion capture hole being less than, suppresses e-/h+It is compound;(b) doped energy-band is formed, less energy can excite Captured on doped energy-band and hole, improve the utilization rate of photon;(c) lattice defect and distortion of lattice are caused, is advantageously formed More Ti3+Oxidation center, so as to expand the photoresponse scope of titanium dioxide, suppress the compound of electronics and hole, and then improve The photocatalysis performance of titanium dioxide compound.
Product of the present invention is applied in tetracycline wastewater processing.
Double rare earth codoping titanium oxide catalyst products of tetracycline wastewater processing.
The performance evaluation of double rare earth codoping titanium dioxide nano materials is carried out in quartz glass tube, 100mL tetracyclines Photochemical catalyst is added in waste water, catalyst amount 1mg/mL, after xenon source catalytic degradation 120min, measure waste water is catalyzed Front and rear TOC, photocatalytic activity of the photochemical catalyst to tetracycline wastewater is calculated.
The present invention is advantageous in that:Two kinds of equimolar proportion rare earth ions are evenly dispersed in aqua oxidation titanium gel In, above-mentioned gel is subjected to hydro-thermal process, washing, filtering and drying, obtains double rare-earth elements doped titanium dioxide photocatalyst afterwards Product.The voluntarily regulation and control that acid-base value is carried out to reaction system are slowly decomposed by urea in water-heat process, realize rare earth element pair The purpose of titanium dioxide codope.The preparation method simple process, Parameter adjustable scope is wide, and repeatability is strong, and cost is low, is made Titanium dioxide optical catalyst there is preferable degradation effect under visible light conditions to tetracycline wastewater.
Brief description of the drawings
Fig. 1 is neodymia/yittrium oxide codope titanium dioxide composite nano materials obtained by embodiment 2.
Embodiment
Embodiments of the invention are elaborated below:The present embodiment is carried out lower premised on technical solution of the present invention Implement, give detailed embodiment and operating process, but protection scope of the present invention is not limited to following embodiments:
Embodiment 1
(1)Urea, cetyl trimethylammonium bromide are added in ethylene glycol(CTAB), cerous nitrate, lanthanum nitrate, after stirring and dissolving Add liquid phase titanium source(Butyl titanate), stir and form homogeneous phase solution.Then deionization is added dropwise while stirring in above-mentioned system Water, until forming clear gel.
(2)Above-mentioned gel is put into the stainless steel autoclave of teflon lined, the hydro-thermal reaction 24h at 150 DEG C. Reaction terminate after precipitated product is washed with deionized, until cleaning solution pH in neutrality, then at 80 DEG C dry 10h with On, processing is dried, dry sample is calcined 2h at 400 DEG C, removes residual organic matter, obtain object lanthana/ Cerium oxide codope titanium dioxide composite nano materials.
Wherein, the titanate esters of the addition and CTAB molar ratio are 1:0.5, the molar ratio of titanate esters and water is 1: 2000.The molar ratio of titanate esters and ethylene glycol is 1:1000, the molar ratio of titanate esters and urea is 1:20.Titanate esters and nitre Sour lanthanum, the molar ratio of cerous nitrate are 1:0.025:0.025.
Photochemical catalyst is 33.6% to tetracycline wastewater TOC degradation rate.
Embodiment 2
(1)Urea, cetyl trimethylammonium bromide are added in ethylene glycol(CTAB), neodymium nitrate, yttrium nitrate, after stirring and dissolving Add liquid phase titanium source(Isopropyl titanate), stir and form homogeneous phase solution.Then deionization is added dropwise while stirring in above-mentioned system Water, until forming clear gel.
(2)Above-mentioned gel is put into the stainless steel autoclave of teflon lined, the hydro-thermal reaction 8h at 200 DEG C. Reaction terminate after precipitated product is washed with deionized, until cleaning solution pH in neutrality, then at 80 DEG C dry 10h with On, processing is dried, dry sample is calcined 2h at 400 DEG C, removes residual organic matter and obtains object neodymia/oxygen Change yttrium codope titanium dioxide composite nano materials.
Wherein, the titanate esters of the addition and CTAB molar ratio are 1:1, the molar ratio of titanate esters and water is 1: 1000.The molar ratio of titanate esters and ethylene glycol is 1:2000, the molar ratio of titanate esters and urea is 1:20.Titanate esters and nitre Sour neodymium, the molar ratio of yttrium nitrate are 1:0.05:0.05.
Photochemical catalyst is 36.2% to tetracycline wastewater TOC degradation rate.
Embodiment 3
(1)Urea, cetyl trimethylammonium bromide are added in ethylene glycol(CTAB), thulium nitrate, gadolinium nitrate, after stirring and dissolving Add liquid phase titanium source(Tetraethyl titanate), stir and form homogeneous phase solution.Then deionization is added dropwise while stirring in above-mentioned system Water, until forming clear gel.
(2)Above-mentioned gel is put into the stainless steel autoclave of teflon lined, the hydro-thermal reaction 12h at 180 DEG C. Reaction terminate after precipitated product is washed with deionized, until cleaning solution pH in neutrality, then at 80 DEG C dry 10h with On, processing is dried, dry sample is calcined 2h at 400 DEG C, removes residual organic matter and obtains object thulium oxide/oxygen Change gadolinium codope titanium dioxide composite nano materials.
Wherein, the titanate esters of the addition and CTAB molar ratio are 1:1, the molar ratio of titanate esters and water is 1: 2000.The molar ratio of titanate esters and ethylene glycol is 1:2000, the molar ratio of titanate esters and urea is 1:40.Titanate esters and nitre Sour thulium, the molar ratio of gadolinium nitrate are 1:0.15:0.15.
Photochemical catalyst is 44.9% to tetracycline wastewater TOC degradation rate.
Embodiment 4
(1)Urea, cetyl trimethylammonium bromide are added in ethylene glycol(CTAB), erbium nitrate, ytterbium nitrate, after stirring and dissolving Add liquid phase titanium source(Isopropyl titanate), stir and form homogeneous phase solution.Then deionization is added dropwise while stirring in above-mentioned system Water, until forming clear gel.
(2)Above-mentioned gel is put into the stainless steel autoclave of teflon lined, the hydro-thermal reaction 15h at 160 DEG C. Reaction terminate after precipitated product is washed with deionized, until cleaning solution pH in neutrality, then at 80 DEG C dry 10h with On, processing is dried, dry sample is calcined 2h at 400 DEG C, removes residual organic matter and obtains object erbium oxide/oxygen Change ytterbium codope titanium dioxide composite nano materials.
Wherein, the titanate esters of the addition and CTAB molar ratio are 1:1, the molar ratio of titanate esters and water is 1: 2000.The molar ratio of titanate esters and ethylene glycol is 1:1500, the molar ratio of titanate esters and urea is 1:30.Titanate esters and nitre Sour erbium, the molar ratio of ytterbium nitrate are 1: 0.05:0.05.
Photochemical catalyst is 41.8% to tetracycline wastewater TOC degradation rate.

Claims (7)

  1. A kind of 1. double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing, with titanate esters, cetyl three Methyl bromide ammonium(CTAB), water, ethylene glycol, urea, rare earth nitrades be raw material, wherein, described titanate esters are liquid phase titanium source, Comprise the following steps:
    (1)Urea, CTAB, two kinds of rare earth nitrades are added in ethylene glycol, liquid phase titanium source is added after stirring and dissolving, stirring is formed Homogeneous phase solution, deionized water is then added dropwise while stirring in above-mentioned system, until formed clear gel, titanate esters and two kinds it is dilute The mol ratio of native nitrate is 1:0.025:0.025~1:0.15:0.15;
    (2)Above-mentioned gel is put into the stainless steel autoclave of teflon lined, at 150 ~ 200 DEG C hydro-thermal reaction 8 ~ Precipitated product is washed with deionized after terminating for 24h, reaction, until the pH of cleaning solution is in neutrality, the then drying at 80 DEG C More than 10h, processing is dried, dry sample is calcined 2h at 400 DEG C, it is double dilute that removing residual organic matter obtains object Native codope titanium dioxide composite nano materials.
  2. 2. double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing according to claim 1, its feature It is, described rare earth nitrades are hydration or non-hydrated cerous nitrate, lanthanum nitrate, neodymium nitrate, yttrium nitrate, gadolinium nitrate, nitric acid Any two kinds in europium, terbium nitrate, samaric nitrate, thulium nitrate, erbium nitrate, ytterbium nitrate.
  3. 3. double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing according to claim 1, its feature It is, it is characterised in that:Titanate esters, CTAB, water, the mol ratio of ethylene glycol and urea are 1:0.5~1:1000~2000:1000 ~2000:20~40.
  4. 4. the double rare earth codoping titanium oxide catalyst preparation methods handled according to the tetracycline wastewater of claim 1 or 3, it is special Sign is that described liquid phase titanium source refers to:One or both of tetra-n-butyl titanate, isopropyl titanate, tetraethyl titanate with On liquid phase titanium source mixture.
  5. 5. double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing according to claim 1, its feature It is, the molar ratio of two kinds of rare earth elements is 1:1.
  6. A kind of 6. double rare earth codopes two of the tetracycline wastewater processing obtained according to any preparation methods of claim 1-5 Titanium oxide catalyst product.
  7. 7. application of the product in tetracycline wastewater processing according to claim 6.
CN201710640852.0A 2017-07-31 2017-07-31 Double rare earth codoping titanium oxide catalyst preparation methods of tetracycline wastewater processing Pending CN107376891A (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108744716A (en) * 2018-04-21 2018-11-06 韩芳 A kind of strainer for efficiency air cleaning device
CN108840390A (en) * 2018-06-26 2018-11-20 韩芳 A kind of environment-friendly high-efficiency sewage treatment process
CN109179796A (en) * 2018-11-23 2019-01-11 陆树旺 Absorption/flocculation/photocatalysis composite dye waste water treating agent and wastewater treatment method
CN110743579A (en) * 2019-11-07 2020-02-04 西安科技大学 Cu2O@TiOF2/TiO2Photocatalyst and preparation method and application thereof
CN111013565A (en) * 2019-12-25 2020-04-17 常州大学 Ytterbium-erbium doped titanium dioxide/attapulgite nanocomposite material and preparation method and application thereof
CN113042028A (en) * 2021-03-26 2021-06-29 福州大学 Preparation method of immobilized Y and Yb double-doped titanium dioxide porous film
CN118619550A (en) * 2024-07-05 2024-09-10 潮州市潮安区雅莱尔陶瓷有限公司 A method for preparing antibacterial porcelain glaze

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102059110A (en) * 2010-12-02 2011-05-18 上海纳米技术及应用国家工程研究中心有限公司 Preparation method of double-rare earth co-doped nanometer titanium dioxide photocatalyst
CN102992397A (en) * 2012-12-13 2013-03-27 上海纳米技术及应用国家工程研究中心有限公司 Preparation method for rare earth element-doped titanium dioxide nano material
CN104289243A (en) * 2014-09-09 2015-01-21 上海纳米技术及应用国家工程研究中心有限公司 Titanium dioxide/quartz fiber photocatalyst with visible-light activity and preparation and application thereof
CN104368326A (en) * 2014-11-14 2015-02-25 湖南稀土金属材料研究院 Preparation method of titanium-dioxide photocatalyst codoped with rare-earth ions
CN105399052A (en) * 2015-11-09 2016-03-16 上海纳米技术及应用国家工程研究中心有限公司 Dual-rare earth-co-doped titanium dioxide gas sensitive sensing material preparation
CN106830071A (en) * 2017-03-09 2017-06-13 吉林大学 A kind of preparation method of the spherical nano titanium oxide doped with rare earth

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102059110A (en) * 2010-12-02 2011-05-18 上海纳米技术及应用国家工程研究中心有限公司 Preparation method of double-rare earth co-doped nanometer titanium dioxide photocatalyst
CN102992397A (en) * 2012-12-13 2013-03-27 上海纳米技术及应用国家工程研究中心有限公司 Preparation method for rare earth element-doped titanium dioxide nano material
CN104289243A (en) * 2014-09-09 2015-01-21 上海纳米技术及应用国家工程研究中心有限公司 Titanium dioxide/quartz fiber photocatalyst with visible-light activity and preparation and application thereof
CN104368326A (en) * 2014-11-14 2015-02-25 湖南稀土金属材料研究院 Preparation method of titanium-dioxide photocatalyst codoped with rare-earth ions
CN105399052A (en) * 2015-11-09 2016-03-16 上海纳米技术及应用国家工程研究中心有限公司 Dual-rare earth-co-doped titanium dioxide gas sensitive sensing material preparation
CN106830071A (en) * 2017-03-09 2017-06-13 吉林大学 A kind of preparation method of the spherical nano titanium oxide doped with rare earth

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108744716A (en) * 2018-04-21 2018-11-06 韩芳 A kind of strainer for efficiency air cleaning device
CN108744716B (en) * 2018-04-21 2020-07-10 安徽昊华环保科技有限公司 Filter screen for efficient air purification device
CN108840390A (en) * 2018-06-26 2018-11-20 韩芳 A kind of environment-friendly high-efficiency sewage treatment process
CN108840390B (en) * 2018-06-26 2021-05-25 广东华水建设工程有限公司 Environment-friendly efficient sewage treatment process
CN109179796A (en) * 2018-11-23 2019-01-11 陆树旺 Absorption/flocculation/photocatalysis composite dye waste water treating agent and wastewater treatment method
CN110743579A (en) * 2019-11-07 2020-02-04 西安科技大学 Cu2O@TiOF2/TiO2Photocatalyst and preparation method and application thereof
CN110743579B (en) * 2019-11-07 2022-08-12 西安科技大学 A Cu2O@TiOF2/TiO2 photocatalyst and its preparation method and application
CN111013565A (en) * 2019-12-25 2020-04-17 常州大学 Ytterbium-erbium doped titanium dioxide/attapulgite nanocomposite material and preparation method and application thereof
CN111013565B (en) * 2019-12-25 2022-03-22 常州大学 Ytterbium erbium doped titanium dioxide/attapulgite nanocomposite material and preparation method and application thereof
CN113042028A (en) * 2021-03-26 2021-06-29 福州大学 Preparation method of immobilized Y and Yb double-doped titanium dioxide porous film
CN118619550A (en) * 2024-07-05 2024-09-10 潮州市潮安区雅莱尔陶瓷有限公司 A method for preparing antibacterial porcelain glaze

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