CN101049961B - Method for preparing sol of high active Nano titanium dioxide - Google Patents
Method for preparing sol of high active Nano titanium dioxide Download PDFInfo
- Publication number
- CN101049961B CN101049961B CN 200710028083 CN200710028083A CN101049961B CN 101049961 B CN101049961 B CN 101049961B CN 200710028083 CN200710028083 CN 200710028083 CN 200710028083 A CN200710028083 A CN 200710028083A CN 101049961 B CN101049961 B CN 101049961B
- Authority
- CN
- China
- Prior art keywords
- sol
- titanium dioxide
- hours
- slurry
- stirred
- 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.)
- Active
Links
Images
Landscapes
- Inorganic Compounds Of Heavy Metals (AREA)
- Catalysts (AREA)
Abstract
This invention discloses a method for preparing highly active titanium dioxide nanosol. The method comprises: (1) weighing titanium oxysulfate or titanium sulfate, adding water to dissolve, dropping base solution to adjust the pH value to above 8, and stirring adequately; (2) filtering, washing the precipitate until there is no sulfate ions, and repeatedly washing with distilled water to neutrality; (3) adding water to the precipitate, mixing uniformly, beating, transferring the slurry to a constant-temperature reaction kettle, adding water, mixing uniformly, dropping acid solution to adjust the pH value to 0.5-2.0, and stirring adequately at normal temperature; (4) stirring the slurry at 40-95 deg.C for 3-60 h; (5) performing high-pressure hydrothermal treatment. The obtained titanium dioxide nanosol is light blue, and does not have any odor or organic matter. Besides, the titanium dioxide nanosol has such advantages as high stability, high crystallinity, high activity, high light transmittance rate, low electron-cavity recombination, high antibacterial and moldproof ability, and no corrosion to matrix. The method has such advantages as simple process and easy operation.
Description
Technical field
The present invention relates to the nano titanic oxide sol technical field, specifically, relate to a kind of preparation method of sol of high active Nano titanium dioxide.
Background technology
Titanium dioxide has very high photocatalytic activity because of it, has anticorrosive, stable in properties, advantage such as nontoxic simultaneously, becomes in recent years the most widely used semiconductor material of photocatalysis field both at home and abroad.In recent years, along with growth in the living standard, people also improve gradually to healthy and environment requirement, therefore sharply expand in the domestic and international market of optically catalytic TiO 2 product aspect indoor air purification, and especially novel photocatalysis air purifying machine and photochemical catalysis spray have occupied most of share in this market.Therefore, the highly active photocatalysis material of titanium dioxide of development and production and expand its Application Areas and not only help improving photochemical catalysis industry utilisation technology also meets the demand in market.
Nano titanium dioxide crystal colloidal sol has stable homogeneous, active high, plurality of advantages such as adhesive power is strong, easy to use, therefore becomes the technical products of the main flow in photocatalyst spray field in recent years.The preparation method of TiO 2 sol has many bibliographical informations, simpler and easy and method that have an application potential mostly is that (＜100 ℃) adopt chemical precipitation-dispergation legal system to be equipped with colloidal sol under the cold condition, as J.Colloid Interf.Sci.260 (2003) 82, reported employing Ti (OBu) respectively among Mater.Sci.Eng.C 15 (2001) 183, J.Euro.Ceram.Soc.18 (1998) 2175 and the J.Sol-Gel Sci.Technol.25 (2002) 121
4, Ti (OC
2H
5)
4, Ti (OC
3H
7)
4, TiCl
4Deng being titanium material, with HNO
3, HCl, perhaps TANOHs is the synthetic colloidal sol of dispergator.In addition, as patent 200510061118,200510126256,200610036598 etc. all is report over nearly 1 year, this study group is devoted to the research and development and the industrialization of this product always, relevant patent (application number is 200410077615,200510037505 national patent, and U.S. Pat Attorney Docket No.16319B and Japanese Patent JP2006-128386) was once arranged before.It is synthetic under the normal pressure that these methods mostly are, mild condition, easy handling, but along with the continuous development of this industry, the quality and the active requirement of this product also improved constantly, therefore require further improvement technology, with the activity of enhancing product performance, to adapt to the demand of market and development.
The relative technological products that most of in the past patent relates to is often after simple relatively technology is synthetic, do not carry out more advanced treatment to improve its performance activity, therefore there are some shortcomings in colloidal sol, and a part contains organism or raw material has strong volatility, easily pollutes, in addition, crystallization degree is not high, impurity (ionogen etc.) content height, and acidity is strong or alkalescence is stronger, have certain corrodibility, the following activity of the dark attitude or the low light level is low etc.Therefore, this product needed further improves the performance and the activity of each side by the advanced treatment technology.
Summary of the invention
The objective of the invention is to overcome the deficiency that exists on the existing nano titanic oxide sol technology of preparing, a kind of preparation method of sol of high active Nano titanium dioxide is provided, utilizes nano titanic oxide sol crystallization degree height, transmittance height, the anti-microbial activity of this method preparation good.
A kind of preparation method of sol of high active Nano titanium dioxide comprises the steps:
(1) take by weighing titanyl sulfate or titanium sulfate, be dissolved in water, dripping alkali liquid is regulated pH greater than 8, fully stirs;
(2) filter, washing precipitation till the sulfate radical-free ion, and then with the distilled water repetitive scrubbing to neutrality;
(3) precipitation is added water mixing, making beating, then slurry is transferred to the thermostatically heating reactor, add the water mixing, drip acid solution, making pH is 0.5～2.0, and normal temperature fully stirs down;
(4) slurry was stirred 3～60 hours down in 40～95 ℃, promptly get nano titanic oxide sol with certain crystallization degree;
(5) nano titanic oxide sol that will have certain crystallization degree is transferred in the airtight withstand voltage reactor, and pressure-controlling is 1 * 10
5～5 * 10
6Pa, temperature is controlled between 50～300 ℃, and be 0.5～20 hour heat-up time, promptly gets sol of high active Nano titanium dioxide.
In above-mentioned preparation method, the described pressure-controlling of step (5) preferred 10
5～10
6Pa.
In above-mentioned preparation method, antibiotic and the mildew-resistant ability for the sterilization that improves nano titanic oxide sol, can carry out noble metal loading to nano titanium oxide handles, its concrete grammar is: add precious metal salt solution in the gained nano titanic oxide sol, placed under the UV-light radiation then 0.5～10 hour, constantly stir simultaneously, wherein deposition should be between 0.1～5%.The salts solution of the preferred gold and silver of described precious metal salt solution, platinum, palladium or rhodium.
In above-mentioned preparation method, in order to reduce the content of nano titanic oxide sol impurity, improve transmittance, reduce electron-hole recombination, can carry out dialysis or nanofiltration processing to nano titanic oxide sol, molecular weight is dammed in dialysis should be between 5000～20000, and dialyzate is selected the pure water of pH between 6～8 for use, and finally regulate the pH value less than 7, to guarantee the stability of colloidal sol.
In above-mentioned preparation method, the preferred sodium hydroxide of the described alkali lye of step (1), potassium hydroxide or ammoniacal liquor.
In above-mentioned preparation method, the preferred hydrochloric acid of the described acid solution of step (3), nitric acid, acetic acid or phosphoric acid; The best is nitric acid or hydrochloric acid.
Compared with prior art, the present invention has following beneficial effect:
1. the TiO 2 sol of the present invention's preparation is light blue, and odorlessness does not contain organism.
2. the TiO 2 sol good stability of the present invention's preparation can not flocculate or precipitate after placement for a long time or the dilution.
3. the TiO 2 sol of the present invention's preparation improves through high pressure water thermal treatment post crystallization degree, the active raising.
4. the TiO 2 sol of the present invention's preparation significantly reduces through dialysis processing rear impurity content, and transmittance improves, and easily causes the surface deposition impurity minimizing of electron-hole recombination or disappears active raising.
5. the TiO 2 sol of the present invention preparation is handled the antibiotic and mildew-proof function of back sterilization through noble metal loading and is significantly improved, and the especially dark attitude or the low light level improve more obvious down.
6. the TiO 2 sol of the present invention's preparation is neutral, can not cause any corrosion to base material, and is applied widely.
7. preparation process technology of the present invention is simple, is convenient to operation, and can require to produce the product of different qualities according to difference, thereby is easy to carry out scale operation.
Description of drawings
Fig. 1 is the transmittance spectrogram of TiO 2 sol at high pressure water thermal treatment different time;
Fig. 2 is the XRD spectra contrast before and after the TiO 2 sol dialysis;
Fig. 3 is the transmittance spectrogram contrast before and after the TiO 2 sol dialysis;
Fig. 4 is the INFRARED SPECTRUM comparison diagram (FTIR) before and after the TiO 2 sol dialysis;
Fig. 5 is the TiO 2 sol of high pressure Hydrothermal Preparation and the active comparison diagram that normal pressure prepares colloidal sol.
Embodiment
Below by embodiment the present invention is further specified.
Take by weighing titanyl sulfate, add water and be stirred to transparently, dropping sodium is regulated more than the pH to 9, continues to stir more than 2 hours, filtration washing (detects with the titration of 0.5M barium chloride solution) till the sulfate radical-free ion repeatedly then, and then with the distilled water repetitive scrubbing to neutrality.At last filter cake is added water mixing, making beating, then slurry is transferred to the thermostatically heating reactor with double-jacket, add the water mixing, drip acid solution then, making pH is 1.2, and normal temperature stirs more than 2 hours down.Carry out dispergation then, slurry in 75 ℃ of following heated and stirred, is promptly obtained having the nano titanic oxide sol of certain crystallization degree after 24 hours; It is transferred in the airtight withstand voltage reactor then, pressure-controlling is 5 * 10
5Pa, temperature is controlled at 140 ℃, and be can obtain nano titanic oxide sol in 2,4,6 or 8 hours heat-up time.Its transmittance changing conditions as shown in Figure 1, the result shows that transmittance slightly descends along with prolong airtight heat-up time, therefore, therefore, will improve the crystallization degree of sol particle on the one hand by the high pressure hydro-thermal; Can not superheated become muddy even precipitation on the other hand to prevent colloidal sol.
The purification and impurity removal and the pH regulator of the TiO 2 sol of embodiment 2. high pressure Hydrothermal Preparation take by weighing titanyl sulfate, adding water is stirred to transparent, dropping ammonia is regulated more than the pH to 9, continue to stir more than 2 hours, filtration washing (detects with the titration of 0.5M barium chloride solution) till the sulfate radical-free ion repeatedly then, and then with the distilled water repetitive scrubbing to neutrality.At last filter cake is added water mixing, making beating, then slurry is transferred to the thermostatically heating reactor with double-jacket, add the water mixing, drip acid solution then, making pH is 1.0, and normal temperature stirs more than 2 hours down.Carry out dispergation then, slurry in 65 ℃ of following heated and stirred, is promptly obtained having the nano titanic oxide sol of certain crystallization degree after 20 hours; It is transferred in the airtight withstand voltage reactor then, pressure-controlling is 10
6Pa, temperature is controlled at 160 ℃, and be 1 hour heat-up time, can obtain nano titanic oxide sol.Adopt dialysis mode (its dam molecular weight should between 8000～12000), remove foreign ion (as nitrate ion, sulfate ion, ammonia radical ion etc.) wherein, it is 6 pure water that dialyzate is selected pH for use, and finally regulates the pH value and should be 5 to guarantee the stability of colloidal sol.
The spectroscopic analysis and the structural analysis of the TiO 2 sol before and after embodiment 3. purification and impurity removals
In order to show the performance variation of handling front and back among the embodiment 2 by dialysis, we have carried out XRD to it, the test of ultraviolet-visible light transmittance spectrum and infrared (FTIR).Fig. 2 is the XRD spectra before and after the TiO 2 sol dialysis, and the result shows before the dialysis except the diffraction peak of anatase octahedrite, to also have several very sharp-pointed diffraction peaks (shown in S among the figure), the reference standard collection of illustrative plates, and it is by NaNO as can be known
3, Na
2SO
4Crystallization Deng sodium salt (NaX) causes, and this is that dispergator (nitric acid) and raw material residual impurity in the preparation process causes.And after the dialysis (shown in After among the figure), these impurity diffraction peaks all weaken greatly even disappear, and the diffraction peak of anatase octahedrite is very clear.
Fig. 3 is the transmittance spectrogram before and after the TiO 2 sol dialysis.The result shows that the transmittance in the zone of colloidal sol more than 350nm obviously improves after the dialysis, and this shows that the dialysis processing also can reduce the particle diameter of colloidal particle simultaneously and then improve transmittance in removal of impurities, and this more helps colloidal sol and in use improves quality of forming film.
Fig. 4 is the infrared spectrum (FTIR) before and after the TiO 2 sol dialysis.The result shows that colloidal sol is at 1385cm after the dialysis
-1The peak area that (the coupled vibration peak that produces for nitrate radical) located reduces greatly, this show dialysis handle removed most of because of adding the nitrate ion that dispergator is introduced; In addition, 835cm
-1, 1789cm
-1, 2423cm
-1The several little vibration peak at place also weakens after dialysis is handled or disappears, this shows that the dialysis processing has significantly reduced the deposition of surface impurity species, help reducing the compound of the electron hole of causing because of impurity in the light-catalyzed reaction process, and then improve reactive behavior.
The specific activity that the TiO 2 sol of embodiment 4. high pressure Hydrothermal Preparation and normal pressure prepare colloidal sol
The photochemical catalysis gas reactor that volume is 33.4L is adopted in this experiment, and built-in three ultraviolet lamps (Philips, 8W, 365nm).Catalyzer is apart from fluorescent tube 1.5cm.Gas to be measured is not thiomethyl alcohol, adopts thiomethyl alcohol transmitter (the Detcon DM-100-CH of Teco Corp.
3SH) test concentrations.Appropriateness is controlled at 52 ± 2% in the experimentation, and temperature is controlled at 25 ± 1 ℃, and catalyst levels 0.5g, area are 18cm * 26cm, and this catalyzer was in 70 ℃ of dryings 24 hours before the test.The active comparative result that the TiO 2 sol and the normal pressure of high pressure Hydrothermal Preparation prepared colloidal sol as shown in Figure 5, clearly, colloidal sol after the high pressure water thermal treatment is active obviously to be improved, degradation rate constant improves above 30%, this mainly is because high pressure water thermal treatment can improve the crystallization degree of nanoparticle, and then improves that it is active.
The TiO 2 sol of embodiment 5. precious metal deposition of silver high pressure Hydrothermal Preparation
Take by weighing titanyl sulfate, add water and be stirred to transparently, dripping alkali liquid is regulated more than the pH to 9, continues to stir more than 2 hours, filtration washing (detects with the titration of 0.5M barium chloride solution) till the sulfate radical-free ion repeatedly then, and then with the distilled water repetitive scrubbing to neutrality.At last filter cake is added water mixing, making beating, then slurry is transferred to the thermostatically heating reactor with double-jacket, add the water mixing, drip acid solution then, making pH is 1.0, and normal temperature stirs more than 2 hours down.Carry out dispergation then, slurry in 65 ℃ of following heated and stirred, is promptly obtained having the nano titanic oxide sol of certain crystallization degree after 20 hours; It is transferred in the airtight withstand voltage reactor then, pressure-controlling is 10
6Pa, temperature is controlled at 160 ℃, and be can obtain nano titanic oxide sol in 1 hour heat-up time.Add silver nitrate solution then in the pure colloidal sol that has prepared, placed under the UV-light radiation then 4 hours, constantly stir simultaneously, wherein deposition is 0.8%.
If will improve the pH value and the removal foreign ion (as nitrate ion, sulfate ion, sodium ion or ammonia radical ion etc.) wherein of colloidal sol, need to adopt modes such as dialysis or nanofiltration (it is minimum dam molecular weight should less than 5000), and finally regulate pH value should be less than 7 stability with assurance colloidal sol.
The corrosion test of front and back to canned bottle handled in embodiment 6. diasolysises
Test method:
Canned bottle is an aluminum alloy material, and whole bottle does not have the slit of welding and pressing, and test material is the colloidal sol that acidic sol (handling without dialysis) and purifying treatment are crossed.
Process of the test is as follows: the colloidal sol that a certain amount of acidic sol and purifying treatment are crossed is poured into respectively in A, the B jar, seal with preservative film, be placed on homo(io)thermism in 60 ℃ water-bath, observed corrosion situation and the colloidal sol outward appearance and the transmittance changing conditions of canned bottle every 24 hours.
Through about 60 days viewing tests, obtain test-results:
(1) since the 7th day, corrosion phenomenon at first appearred in the A bottle, and the colloidal sol transmittance descends in the bottle, and muddy sign is arranged; By the 10th day, colloidal sol was relatively more muddy, and deposited phenomenon occurs;
(2) arrive the 8th day, corrosion phenomenon does not take place in B bottle inside, and colloidal sol outward appearance and transmittance all do not have considerable change in the bottle;
When (3) arriving 15 days, in the A bottle corrosion comparatively serious, colloidal sol is precipitation substantially fully, has therefore ended the test of A bottle, still do not have considerable change in the B, and the colloidal sol outward appearance still keeps good;
(4) arrive the 45th day, all do not see obvious corrosion in the B bottle, colloidal sol still keeps stable and does not precipitate, and colloidal sol does not still have considerable change in the B bottle;
(5) arrive the 60th day, all do not see obvious corrosion in the B bottle, colloidal sol still keeps stable and does not precipitate, and colloidal sol does not still have considerable change in the B bottle.
The sterilization effect evaluation of embodiment 7. precious metal deposition of silver TiO 2 sols
Test foundation and analytical procedure: antibacterial and bactericidal property and stability test method with reference to appendix C product among the GB 15979-2002, the gene test method among the QB/T2591-2003.
Test microbes: colon bacillus, streptococcus aureus, Pseudomonas aeruginosa and e coil k 1 pneumonia germ.
Test condition:
25 ℃ of a, culture temperature.
UV-light activation colloidal sol and substratum mixed system are 1 hour before b, the inoculation.Inoculate bacterial classification to be measured then, cultivate in the incubator.Do the blank experiment simultaneously
Be calculated as follows the antibacterium rate:
Pure TiO
2Colloidal sol and deposition of silver TiO
2The anti-microbial activity result such as the following table of colloidal sol:
Table 1 anti-microbial property detected result
By data in the table 1 as seen, deposition of silver TiO
2Colloidal sol all is higher than pure TiO to the anti-microbial activity of colon bacillus, streptococcus aureus, Pseudomonas aeruginosa and these four kinds of bacterium of e coil k 1 pneumonia germ
2Colloidal sol can reach complete germ-resistant effect substantially in 24 hours.
Embodiment 8. deposition of silver TiO
2The mildew-resistant level estimate of colloidal sol
Test bacterial classification: mix the mould bacterial classification, comprise aspergillus niger (Aspergillus niger) ATCC16404, flavus (Asp.flavus) GIM3.17, Sai Shi aspergillus (Asp.sydowii) GIM1.01, terreus (Asp.terreus) GIM3.34, Aspergillus ustus (Asp.ustus) GIM3.40, bud branch mould (Chaetomium herbarum) GIM3.57, paecilomyces varioti (Paecilomycesvarioti) GIM3.385, Chaetomium globosum (Chaetomium globasum) GIM3.52, Penicillium citrinum (penicillium citrinum) GIM3.100, viride (Trichoderma viride) GIM3.139.
Incubation time: 14 days, ultraviolet activated 1 hour (control experiment does not activate) before the process of the test, and conventional incubator is cultivated.
Assessment by mould proof ability has constituted the mildew-resistant grade, judges by following index:
0---no mildew
1---the mildew spot is in 1 millimeter, and it is sparse to distribute;
2---the mildew spot is in 2 millimeter or spread and be grown in 2 millimeters scopes, mildew maximum 1/4th of the whole surface that is no more than that distributes;
3---the mildew spot accounts for 1/4th of whole surface in 2 millimeter or distribution;
4---the mildew spot is covered with mycelia on more than 5 millimeters or whole surface.
The second stage of pilot scale TiO of table 2
2Colloidal sol mildew-resistant level estimate
Table 2 result shows that if activate through ultraviolet before the catalyst experiment, the mildew-resistant grade of two kinds of colloidal sols has all reached 0 grade, promptly sprayed colloidal sol after, its surface in contact is mildew no longer all, this shows that this colloidal sol product has good mildew-resistant effect under certain photoirradiation.If activate through ultraviolet before the catalyst experiment, pure colloidal sol is owing to reduced activity under the low light level, so the growth of mould fungus inhibition fully, its mildew-resistant grade is 1 grade; And Ag depositing Ti O
2Colloidal sol but still has good anti-mold effect, and its mildew-resistant grade is 0 grade, i.e. mildew not, and this mainly is because surface deposition silver itself has very high bacteriostatic activity, this explanation Ag deposition has improved TiO
2The antimold activity of colloidal sol not only has good anti-mold effect, even also can well play a role under no optical condition under high light, can be widely used in the place of each different illumination intensity.
Claims (2)
1. the preparation method of a sol of high active Nano titanium dioxide is characterized in that comprising the steps:
Take by weighing titanyl sulfate, add water and be stirred to transparently, dropping sodium is regulated more than the pH to 9, continues to stir more than 2 hours; Then repeatedly filtration washing till the sulfate radical-free ion, and then with the distilled water repetitive scrubbing to neutral; At last filter cake is added water mixing, making beating, then slurry is transferred to the thermostatically heating reactor with double-jacket, add the water mixing, drip acid solution then, making pH is 1.2, and normal temperature stirs more than 2 hours down; Carry out dispergation then, slurry in 75 ℃ of following heated and stirred, is promptly obtained having the nano titanic oxide sol of certain crystallization degree after 24 hours; It is transferred in the airtight withstand voltage reactor then, pressure-controlling is 5 * 10
5Pa, temperature is controlled at 140 ℃, and be 2,4,6 or 8 hours heat-up time, can obtain sol of high active Nano titanium dioxide;
Or
Take by weighing titanyl sulfate, add water and be stirred to transparently, dropping ammonia is regulated more than the pH to 9, continues to stir more than 2 hours; Then repeatedly filtration washing till the sulfate radical-free ion, and then with the distilled water repetitive scrubbing to neutral; At last filter cake is added water mixing, making beating, then slurry is transferred to the thermostatically heating reactor with double-jacket, add the water mixing, drip acid solution then, making pH is 1.0, and normal temperature stirs more than 2 hours down; Carry out dispergation then, slurry in 65 ℃ of following heated and stirred, is promptly obtained having the nano titanic oxide sol of certain crystallization degree after 20 hours; It is transferred in the airtight withstand voltage reactor then, pressure-controlling is 10
6Pa, temperature is controlled at 160 ℃, and be 1 hour heat-up time, can obtain sol of high active Nano titanium dioxide.
2. preparation method as claimed in claim 1 is characterized in that, described acid solution is hydrochloric acid, nitric acid, acetic acid or phosphoric acid.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 200710028083 CN101049961B (en) | 2007-05-18 | 2007-05-18 | Method for preparing sol of high active Nano titanium dioxide |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 200710028083 CN101049961B (en) | 2007-05-18 | 2007-05-18 | Method for preparing sol of high active Nano titanium dioxide |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN101049961A CN101049961A (en) | 2007-10-10 |
| CN101049961B true CN101049961B (en) | 2011-04-06 |
Family
ID=38781599
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN 200710028083 Active CN101049961B (en) | 2007-05-18 | 2007-05-18 | Method for preparing sol of high active Nano titanium dioxide |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN101049961B (en) |
Families Citing this family (16)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102078792B (en) * | 2009-11-27 | 2012-12-12 | 中国科学院生态环境研究中心 | Synthesis method and application of nano-titanium dioxide for adsorption of heavy metals |
| CN102077865B (en) * | 2010-11-19 | 2013-12-04 | 华南农业大学 | Titanium dioxide nano particle and litchi nano preservative |
| CN102086046A (en) * | 2010-12-31 | 2011-06-08 | 东莞市明天纳米科技有限公司 | Preparation method of nano-TiO2 lyosol |
| CN103274459A (en) * | 2013-06-08 | 2013-09-04 | 苏州诺信创新能源有限公司 | Titanium dioxide slurry preparation method |
| CN103980738B (en) * | 2014-05-15 | 2015-11-04 | 北京化工大学 | A kind of preparation method of coating modification nano titanium oxide |
| CN105879611B (en) * | 2016-05-09 | 2019-11-08 | 西安天宇环保科技有限公司 | The preparation method of nanotechnology formaldehyde scavenger |
| CN106927949A (en) * | 2017-03-21 | 2017-07-07 | 广东省生态环境技术研究所 | A kind of selenium dopen Nano titanium colloidal sol for degrade agricultural product Pesticides and heavy metal and its preparation method and application |
| CN107814413B (en) * | 2017-11-10 | 2019-07-30 | 纳琦环保科技有限公司 | The preparation method of water nano titanium oxide sol |
| CN108101584A (en) * | 2017-12-28 | 2018-06-01 | 洛阳名力科技开发有限公司 | A kind of preparation method of anti-bacteria ceramic |
| CN108585146B (en) * | 2018-04-28 | 2020-12-11 | 宁波新福钛白粉有限公司 | Preparation method of titanium-containing composite ferric polysulfate flocculant |
| CN110171847A (en) * | 2019-05-17 | 2019-08-27 | 安徽迪诺环保新材料科技有限公司 | Preparation method, product and its application of nano-titanium dioxide |
| CN113896228B (en) * | 2020-07-06 | 2023-08-11 | 极微纳(福建)新材料科技有限公司 | Titanium dioxide material and preparation method and application thereof |
| CN111804143A (en) * | 2020-07-10 | 2020-10-23 | 中触媒新材料股份有限公司 | Three unit UV ambient air purification devices |
| CN113620613A (en) * | 2021-09-09 | 2021-11-09 | 成都先进金属材料产业技术研究院股份有限公司 | Method for preparing titanium-based nano self-cleaning film by taking titanyl sulfate as titanium source |
| CN113695212A (en) * | 2021-09-09 | 2021-11-26 | 成都先进金属材料产业技术研究院股份有限公司 | Method for preparing titanium-based nano anticorrosive film by taking titanyl sulfate as titanium source |
| CN114409965B (en) * | 2022-01-19 | 2024-02-09 | 山东国瓷功能材料股份有限公司 | Functionalized titanium dioxide filler, preparation method thereof and PTFE (polytetrafluoroethylene) high-frequency copper-clad laminate |
-
2007
- 2007-05-18 CN CN 200710028083 patent/CN101049961B/en active Active
Also Published As
| Publication number | Publication date |
|---|---|
| CN101049961A (en) | 2007-10-10 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101049961B (en) | Method for preparing sol of high active Nano titanium dioxide | |
| KR101414899B1 (en) | Photocatalyst titanium oxide sol, and coating composition and member utilizing the same | |
| US7897137B2 (en) | Method for producing high-active titanium dioxide hydrosol by using metatitanate as precursor | |
| CN100484880C (en) | Low-temperature crystallized nano titanium dioxide powder and synthesis method of sol | |
| CN101827650B (en) | Transparent, stable titanium dioxide sols | |
| CN101049962A (en) | Method for preparing sol of neutral Nano titanium dioxide | |
| CN100537434C (en) | Method for preparing Nano sol as ultraviolet protective agent | |
| EP1127844B1 (en) | Finely particulate titanium-containing substance, coating fluid containing the same, processes for producing these, and molded article having thin film comprising the substance | |
| US20110028311A1 (en) | Visible Light Activatable Photocatalyst | |
| CN101773820B (en) | Method for preparing visible light active photocatalyst through dye sensitization | |
| CN105772040B (en) | A kind of composite photocatalyst anti-biotic material and preparation method thereof | |
| CN102219179B (en) | Silver-doped titanium dioxide film and preparation method thereof | |
| Powell et al. | N-doped TiO2 visible light photocatalyst films via a sol–gel route using TMEDA as the nitrogen source | |
| CN102139206B (en) | Preparation method of composite photocatalyst containing nitrogen-doped titanium dioxide and zinc titanate | |
| CN101972653B (en) | Anatase type nano Ag/TiO2Method for preparing composite material | |
| CN104841015B (en) | High-specific-surface-area silver-loaded titanium dioxide composite antibacterial material and preparation method thereof | |
| CN102295310A (en) | Preparation method of metal ion doped titanium dioxide transparent water sol | |
| CN100442982C (en) | Method for preparing nano Ag (I)/Ag (III)/TiO2 composite material | |
| US20110147317A1 (en) | Catalytic Compositions, Composition Production Methods, and Aqueous Solution Treatment Methods | |
| CN100493708C (en) | High-activity phosphor doped peptide oxide light catalyst, its production and use | |
| CN102553620A (en) | Visible light photocatalyst Bi12O17Cl2 and preparation method thereof | |
| CN1454481A (en) | Rare-earth-carrying nano titanium dioxide antibacterial agent and preparation method thereof | |
| CN105271400A (en) | Preparation method of mixed crystal nano-TiO2 | |
| CN1310589C (en) | Method for preparing superfine composite inorganic antimicrobial agent | |
| CN107774284A (en) | The preparation method of water nano antibacterial photocatalysis titanium oxide complex sol |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| ASS | Succession or assignment of patent right |
Owner name: FOSHAN IRONMAN ENVIRONMENTAL TECHNOLOGY CO., LTD. Free format text: FORMER OWNER: GUANGDONG PROV. INST. OF ECOLOGICAL ENVIRONMENT + SOIL SCIENCE Effective date: 20120320 |
|
| C41 | Transfer of patent application or patent right or utility model | ||
| COR | Change of bibliographic data |
Free format text: CORRECT: ADDRESS; FROM: 510650 GUANGZHOU, GUANGDONG PROVINCE TO: 528000 FOSHAN, GUANGDONG PROVINCE |
|
| TR01 | Transfer of patent right |
Effective date of registration: 20120320 Address after: 528000 B3-3, B3-4, third floor, Foshan Torch Innovation and Innovation Park, Jihua Road, Chancheng District, Foshan, Guangdong two, China Patentee after: Foshan iron man Environmental Protection Technology Co., Ltd. Address before: Tianhe District Tianyuan road Guangzhou City, Guangdong province 510650 No. 808 Patentee before: Guangdong Prov. Inst. of Ecological Environment & Soil Science |