METHOD FOR PREPARING A PHOTOCATALYTIC TITANIUM DIOXIDE SUN, NEUTRAL, STABLE AND TRANSPARENT

专利摘要:
neutral, stable and transparent photocatalytic titanium dioxide sols. a method of preparing a photocatalytic, neutral, stable and transparent sol (colloidal suspension) of titanium dioxide is proposed, comprising the following steps: (1) contacting a titanium dioxide sol with an alkaline peptizing agent to obtain a peptized alkaline titanium dioxide sol; (2) neutralize the peptized alkaline titanium dioxide sol and (3) obtain or collect the photocatalytic, neutral, stable and transparent titanium dioxide sol. the titanium dioxide sol is stable and transparent in a pH range of about 7.0 to about 9.5. the titanium dioxide sol can include titanium dioxide crystallites with an average particle size of less than about 10 nm with at least 90% of the crystallites in anatase form.
公开号:BR112014011860B1
申请号:R112014011860-4
申请日:2012-11-16
公开日:2020-12-15
发明作者:Julie Elizabeth Kerrod；Anthony Roy Wagstaff
申请人:Tronox Llc；
IPC主号:

专利说明:

1. TECHNICAL FIELD
[001] The processes, procedure (s), method (s), product (s), inventive result (s) presently described and claimed, and / or concept ( s) (collectively, hereinafter referred to as "the inventive concept (s) presently described and claimed", refer, in general, to compositions that provide a photocatalytic coating. More specifically, the inventive concept (s) presently described and claimed refer to solids (colloidal suspension) of titanium dioxide nanoparticles useful to provide transparent coatings. photocatalytic on a substrate, which are depolluting and / or self-cleaning and may also, in certain embodiments, have anti-bacterial properties. 2. GROUNDS
[002] The photocatalytic properties of the semicon-conducting titanium dioxide material results from the promotion of electrons from the valence range to the conduction range under the influence of ultraviolet (UV) radiation and close to UV radiation. The reactive electron-hole pairs that are created migrate to the surface of the titanium dioxide particles where the holes oxidize the adsorbed water to produce reactive hydroxyl radicals and the electrons reduce the adsorbed oxygen to produce the superoxide radicals, which can degrade the NOx and volatile organic compounds (VOCs) in the air. In view of these properties, photocatalytic titanium dioxide has been used in coatings (both fitted and unattached) and the like, to remove pollutants from the air. These coatings can also have the advantage of being self-cleaning, since dirt (grease, mold, fungi, algae, bacteria, etc.) is also oxidized on the surface.
[003] In many applications, it is desirable for the titanium dioxide coating to be transparent in order to maintain the original appearance of the substrate (eg ceramic tiles, paving blocks, brick, stone, marble countertop for surgical instruments used during medical procedures, solar cells, fabrics and non-fabrics made of natural or synthetic fibers, etc.), or their original transparency (eg window glass, automobile windshields, surgical instruments used for visualization, etc.). ). Colloidal titanium dioxide soles have proven to be useful precursor materials for the formation of these transparent and reactive coatings.
[004] A stable, alkaline titanium dioxide sol can be established at a pH above 11.30. The sun can be used to form coatings that can be applied to buildings, concrete surfaces and highways. However, the sun often has a strong, irritating pungent "ammonia-like" smell and can be flammable under certain conditions. Thus, it is difficult to use a sun like this, without incurring the cost and difficulty of putting on personal protective equipment and at the expense of using extraction technology to remove residual amounts of sun from these areas (such as soil dirt) adjacent to the substrate to be treated. In addition, substrates may react adversely with high pH peptizing agents in the sun.
[005] It is desirable to neutralize the alkaline titanium dioxide sol, so that the sun becomes virtually odorless and non-flammable, thus overcoming many of the aforementioned deficiencies, and allowing that sun to be applied as an aqueous based surface coating. environmentally safe photoactive. However, as the pH of the alkaline titanium dioxide sol is reduced, the colloidal system typically agglomerates and becomes unstable and may even collapse. This agglomeration is irreversible, that is, even if the solution is readjusted back to a high pH, the colloidal stability is not returned. It is, therefore, desirable and researched in the art for a long time, to provide stable neutral soles comprising photocatalytic titanium dioxide, which are reactive, neutral and transparent. It is also desirable that such photocatalytically active, reactive, neutral and transparent colloidal titanium dioxide solutions are stable over an extended period of time and also maintain photoactivity over a period of time and at an activity rate that is above that currently available on the market. It is well known to a person skilled in the art that the creation of a stable, transparent and neutral TiO2 sol is difficult (and has long been sought in industry), due to the natural tendency for TiO2 to flake between the pH values of about 4 to about 10, due to the absence of any electrostatic stabilization that occurs at neutral (or almost neutral) pH. In addition, it is difficult to identify suitable or effective molecules that can act as steric stabilizers in TiO2 solids, due to the extremely small size of TiO2 particles. Since effective steric stabilizers are generally larger molecules, a person skilled in the art has had difficulty identifying suitable steric stabilizers for use. It is also desirable that such photocatalytically active colloidal solutions of reactive, neutral and transparent titanium dioxide have antibacterial and antimicrobial activity. It is also desirable that the concept of the invention presently described and claimed provides new methods for the preparation of such reactive, neutral, stable and transparent soles, which are easily implemented on a commercial scale. SUMMARY OF THE INVENTION
[006] In accordance with the previous objectives and others, it was discovered that the titanium dioxide soles, which are reactive, neutral, stable and transparent, which can be used safely and in an environmentally friendly way , can be formed by neutralizing alkaline titanium dioxide soles in the manner set forth herein.
[007] In an aspect of the inventive concept presently claimed and described, a method is provided for the preparation of a photocatalytic, reactive, neutral, stable and transparent titanium dioxide sol, comprising: (1) the reaction of a gel of titanium dioxide hydrated with an alkaline peptizing agent to provide a peptized alkaline titanium dioxide sol; (2) neutralizing the peptized alkaline titanium dioxide sol; and (3) obtaining or collecting the resulting neutral, stable, transparent photocatalytic titanium dioxide sol.
[008] In another aspect of the inventive concept claimed and disclosed here, a method is provided for the preparation of a reactive, neutral, stable and transparent photocatalytic titanium dioxide suspension, comprising: (1) precipitation titanium dioxide hydrated from a solution containing a compound containing titanium to form the titanium dioxide particles; (2) formation of a dispersion of titanium dioxide particles in a liquid medium; (3) treating the dispersion with an alkaline peptizing agent to obtain a peptized alkaline titanium dioxide sol. (4) neutralization of the peptized alkaline titanium dioxide sol; and (5) obtaining or collecting the resulting neutral, stable, transparent photocatalytic titanium dioxide.
[009] The peptized alkaline titanium dioxide sol can be neutralized by boiling the peptized alkaline titanium dioxide sol by mixing hydrogen peroxide with the peptized alkaline titanium dioxide sol, or by mixing an acidic compound with the sodium dioxide sol peptized alkaline titanium. The acidic compound can comprise, for example, but not by way of limitation, a first acidic compound and a second acidic compound, wherein the first acidic compound and the second acidic compound can be selected from the group consisting of a mineral acid , an organic acid or its combinations.
[010] The resulting titanium dioxide sol is reactive, stable and transparent over a pH range of about 8.5 to about 9.5. The colloidal suspension of stable titanium dioxide may be in the form of titanium dioxide particles having an average size of less than about 50 nm, with crystallites less than about 20 nm, less than about 10 nm, or between about 1 nm and about 10 nm, with the main form of crystallites in the form of anatase. In an alternative embodiment, the crystallites can have an average particle size between about 1 nm and about 5 nm. According to another embodiment, at least 90% of the crystallites are in the form of anatase.
[011] The titanium dioxide of the concept of the invention currently claimed and described is, in one embodiment, greater than 95% by weight in the form of anatase. In other embodiments, the titanium dioxide particles of the inventive concept claimed and disclosed herein have an average particle size less than about 10 nm, or, alternatively, less than 5 nm.
[012] In another embodiment, the inventive concept claimed and disclosed herein comprises titanium dioxide particles with an average particle size less than about 50 nm, in which the sun is transparent and is stable for at least one month, when stored at room temperature. In other embodiments, the sun is stable when stored for at least 2, at least 3 or at least 4 months at room temperature. In yet another embodiment, the sun is stable when stored for at least 5 or at least 6 months at room temperature. In another embodiment, the sun is stable when stored for at least 1 year or at least 2 years at room temperature. In another embodiment of the process the sun has a viscosity of less than about 100 centipoise after at least 4 weeks at room temperature.
[013] Another aspect of the inventive concept presently described and claimed provides a neutral, stable and transparent photocatalytic titanium dioxide sol formed from an alkaline titanium dioxide sol which is peptized and neutralized.
[014] Another aspect of the inventive concept presently described and claimed provides a structure or composition containing reactive, neutralized titanium dioxide soles for use on a substrate for removing NOx under exposure to UV light. The colloidal solutions of the inventive concept claimed and disclosed here have greater stability when compared to commercially available colloidal solutions with similar size and transparency profiles.
[015] Another aspect of the inventive concept presently described and claimed, provides an antibacterial composition comprising the neutral, stable and transparent photocatalytic titanium dioxide sol which, when placed in contact with bacteria, kills at least 80% of the bacteria.
[016] These and other aspects of the inventive concept (s) presently claimed and described (s) will be better understood, making reference to the following detailed description and the attached figures. BRIEF DESCRIPTION OF THE FIGURES
[017] FIG. 1 is a graph that compares the NOx reduction of an alkaline titanium dioxide sol containing DEA treated with different percentages of phosphoric acids, combined with acetic acids under UV radiation.
[018] FIG. 2 is a graph comparing the NOx reduction of an alkaline titanium dioxide sol containing TMAOH (tetramethylammonium hydroxide) treated with different percentages of phosphoric acids, combined with acetic acids under UV radiation.
[019] FIG. 3 is a graph that compares the NOx reduction of an alkaline titanium dioxide sol containing DEA treated with different percentages of phosphoric acids, combined with acetic acids under various light sources.
[020] FIG. 4 is a graph that compares the NOx reduction of an alkaline titanium dioxide sol containing TMAOH as a function of the concentration of phosphoric acid combined with acetic acid under various light sources.
[021] FIG. 5 is a graph comparing the NOx reduction of an alkaline titanium dioxide sol containing DEA (diethylamine) treated with various acids in concrete under UV radiation as a function of time.
[022] FIG. 6 is a graph that compares the NOx reduction of an alkaline titanium dioxide sol containing DEA treated with various acids on a glass substrate under UV radiation as a function of time.
[023] FIG. 7 is a graph that compares the NOx reduction of an alkaline titanium dioxide sol containing DEA after neutralization with concrete acetic and phosphoric acid at different initial NO exposures under UV radiation, as a function of time.
[024] FIG. 8 is a graph that compares the proportions of NO at the baseline with the values measured on a concrete wall coated with a neutralized alkaline titanium dioxide sol containing DEA as a function of time, in the Camden-London area, England.
[025] FIG. 9 is a graph that compares the NO2 values at the baseline with the values measured on a concrete wall coated with a neutralized alkaline titanium dioxide sol containing DEA as a function of time, in the Camden-London area, England.
[026] FIG. 10 is a graph comparing viscosity over time for colloidal solutions of alkaline titanium dioxide containing varying amounts of DEA.
[027] FIG. 11 is a graph comparing viscosity over time for colloidal solutions of alkaline titanium dioxide containing varying amounts of DEA treated with either phosphoric acid or a phosphoric acid / acetic acid mixture.
[028] FIG. 12 is a graph comparing the viscosity of colloidal solutions of alkaline titanium dioxide containing different amounts of DEA and washed with either demineralized water or running water.
[029] FIG. 13 is a graph that compares the quantities of NO at the baseline with the values measured on a concrete wall coated with a neutralized alkaline titanium dioxide sol containing DEA, and with the values measured on a concrete wall covered with wood, as a function of time, in the Camden area of London, England.
[030] FIG. 14 is a graph that compares the NO2 values at the baseline with the values measured on a concrete wall coated with a neutralized alkaline titanium dioxide sol containing DEA, and with the values measured on the concrete wall covered with wood, as a function of time, in the Camden area of London, England. DETAILED DESCRIPTION
[031] Before explaining at least one embodiment of the concepts (s) of the invention disclosed here in detail, it should be understood that, the concept (s) of the invention, process (ies), methodology ( s) and / or result (s) are not limited in its application, to the details of construction and to the availability of the components or steps or methodologies established in the following description or illustrated in the drawings. The concept (s), process (ies), methodology (ies) and / or result (s) of the invention presently described and claimed (s) are susceptible to other forms of realization or can be practiced or performed many ways. Still, it should be understood that the phraseology and terminology used here is intended for the purpose of description and should not be considered as limiting the inventive concept presently described and claimed (s), process (ies), methodology (ies) and / or result - not at all. With respect to any patent reference or otherwise mentioned here, that reference shall be considered incorporated herein by reference in its entirety as if expressly presented here.
[032] All terms used here aim to have their common sense, unless otherwise specified. The term "sol" refers to a colloidal suspension of particles. The term "NOx" refers to species NO (nitrogen oxide) and NO2 (nitrogen dioxide), collectively or individually.
[033] Whenever reference is made to "removing" pollutants from the air, it should be understood to include the complete or partial removal of pollutants from the air. If the removal is "substantial" it can be determined by the methods presented in the examples, where "substantial removal" refers to a reduction in the total concentration of a fixed amount of a given pollutant by at least about 5%, preferably at least about 10 %%, and more preferably, at least about 15%. Given the present description (including the examples), a person skilled in the art will appreciate that the soles of the inventive concept (s) claimed and disclosed herein provide exceptional NOx removal and / or degradation and , in a particular test, the soles of the inventive concept currently claimed and disclosed, offer 60% NO removal and 20% NO2 removal under specific external environmental conditions in London.
[034] The method for the preparation of neutral, stable and transparent soles of colloidal photocatalytic titanium dioxide according to the inventive concepts described and claimed is generally constituted by: (1) reacting a hydrated titanium dioxide gel with an alkaline peptizing agent to provide a peptized alkaline titanium dioxide sol; (2) neutralizing the peptized alkaline titanium dioxide sol; and (3) obtaining or collecting the resulting photocatalytic, reactive, neutral, stable and transparent titanium dioxide sol, which may be mainly in the form of anatase and may have an average particle size less than about 50 nm. In one embodiment, the average size of the titanium dioxide particles is less than or equal to about 20 nm. One skilled in the art will appreciate that the resulting neutral, stable and transparent photocatalytic titanium dioxide sol will be amorphous in nature.
[035] In one embodiment, the alkaline peptizing agent is a mono, di- or trialkylamine; mono-, di- or triarylamine; organic bases with two or more functional groups, such as dialcanolamines and trialcanolamines and the like. Mono di- or trialkylamine peptizing agents may comprise linear, branched or cyclic alkyl groups. Suitable amines include, but are not limited to, mono-, di- or trimethylamine; mono-, di- or triethylamine; mono-, di- or tripropylamine; mono-, di- or tributylamine, sec-butylamine, isobutylamine, isopropylamine, iso-amylamine, tert-amylamine, 2-methylbutylamine, 1-methylbutylamine and similar combinations. In one embodiment, the alkaline peptizing agent is diethylamine.
[036] Amines with cyclic alkyl groups include, but are not limited to: cyclopropylamine, cyclobutylamine, cyclopentylamine, cyclohexylamine, cycloheptylamine and cyclooctylamine, as well as their di- and trialkyl derivatives. Of course, amines with different alkyl groups, such as diisopropylethylamine, ethylbutylamine, methylethylamine, and the like, can be used. Also contemplated are cyclic amines, such as pyrrolidine, piperidine, morpholine, and the like, as well as their N-alkyl derivatives. Preferably, bulky mono-, di- or trialkylamines such as tert-butylamine, triethylamine, propylamine, dipropylamine, diisopropylethylamine, and the like, are used as basic peptizing agents.
[037] In another embodiment, the alkaline peptizing agent can be a quaternary ammonium hydroxide. The quaternary ammonium hydroxide can, in one embodiment, be selected from the group consisting of tetraalkylammonium hydroxide in which the alkyl group contains atoms from C1 to C10 or combinations of atoms C1 through C10. The quaternary ammonium hydroxide can be tetralmethylammonium hydroxide.
[038] The neutralization step of the peptized alkaline titanium dioxide sol can be carried out by boiling the peptized alkaline titanium dioxide sol, mixing the hydrogen peroxide, with the peptized alkaline titanium dioxide sol, or by mixing a acidic compound with the peptized alkaline titanium dioxide sol. The boiling of the peptized alkaline titanium dioxide sol can be conducted at a temperature that removes the alkaline peptizing agent. In one embodiment, the temperature is in the range of about 40 ° C to about 120 ° C. In another embodiment, the temperature is in the range of about 60 ° C to about 110 ° C.
[039] Hydrogen peroxide can react with titanium dioxide to form a stable peroxide complex. Generally, a large amount of hydrogen peroxide is required for neutralization to occur. In one embodiment, about 50% to about 200% hydrogen peroxide is used in relation to the weight of the peptized alkaline titanium dioxide sol. In another embodiment, about 100% to about 150% hydrogen peroxide is used in relation to the weight of the peptized alkaline titanium dioxide sol. One of ordinary skill in the art, in view of the present description, should understand that any specific percentage of hydrogen peroxide can be used as long as neutralization occurs.
[040] The acidic compound can, in one embodiment, be selected from the group consisting of a first acidic compound, a second acidic compound and combinations thereof. The first acidic compound can, in one embodiment, be selected from a mineral acid, an organic acid and their combinations. In one embodiment, mineral acid is phosphoric acid. The organic acid can, in one embodiment, be an aromatic, aliphatic hydroxycarboxylic acid or combinations thereof. Organic acid can be selected from the group consisting of oxalic acid, citric acid, tartaric acid, salicylic acid, and combinations thereof, for example.
[041] The second acidic compound can be a mineral acid, an organic acid or combinations thereof. In one embodiment, the mineral acid is nitric acid. When an organic acid is used, it can be acetic acid. The percentage of the first acidic compound can vary from about 25 to about 100 parts by weight, and the percentage of the second acidic compound can vary from about 0 to about 75 parts by weight, and one skilled in the art would appreciate and be able to adapt these parts, by weight, as needed.
[042] In a particular embodiment, the acidic compound is added dropwise to the sun with peptized alkaline titanium dioxide, while stirring at room temperature. The stirring can be done continuously or intermittently, as long as the functional requirement is satisfied. The final pH value of the resulting neutralized colloidal suspension is, in a given embodiment, controlled to be within a range of about 8 to about 9.
[043] In another aspect of the inventive concept (s) claimed and disclosed here, a method is provided for the preparation of a colloidal suspension of neutral, stable and transparent photocatalytic titanium dioxide that comprises: (1) precipitation of hydrated titanium dioxide from a solution with a compound containing titanium in it to form the titanium dioxide particles; (2) formation of a dispersion of titanium dioxide particles in a liquid medium; (3) treating the dispersion with an alkaline peptizing agent to obtain a peptized alkaline titanium dioxide sol; (4) neutralization of the peptized alkaline titanium dioxide sol, and (5) obtaining or collecting the resulting neutral, stable and transparent photocatalytic titanium dioxide sol.
[044] The compound containing titanium can be any compound capable of forming a precipitate of titanium dioxide. In one embodiment, the compound containing titanium is an organotitanium compound. Suitable organotitanium compounds include, but are not limited to, titanium alkoxides of the general structure Ti (OR) 4 wherein each R is independently alkyl, aryl or heteroaryl; acyl titanium compounds, such as titanyl acetylacetonate and the like. Preferred titanium alkoxides include titanium tetraisopropyl dioxide, titanium tetra-n-propoxide, titanium tetraethoxide, titanium tetraethoxide, titanium tetra-n-butoxide and titanium tert-butoxide and the like. Mixed titanium alkoxides, where the R groups in Ti (OR) 4 may be different, are also contemplated as the compound containing titanium. Other suitable organic titanium compounds include titanium amine (IV) compounds, such as tetra-quench (dimethylamino) titanium, tetrakis (diethylamino) titanium and the like.
[045] Titanium halides represented by the general formula TiX4, where X is chlorine, bromine, iodine or fluorine, or mixtures thereof, can also be used as compounds containing titanium. The concept (s) of the invention presently claimed and described (s) also contemplate the use of organotitanium halides, such as chlorotitanium triisopropoxide (Ti (Oi-Pr) 3CI) and the like, as the compounds containing titanium . Organotitanium di- and trihalides are also contemplated, and although not limited by theory, it is believed that when titanium halides are used as titanium-containing compounds, halides are generally hydrolyzed first in a controlled for a less reactive species, such as titanium oxyhalide (eg, titanium oxychloride and the like). The resulting intermediate titanium species can then be further hydrolyzed to TiO2, by adjusting the pH of the solution.
[046] In another aspect of the inventive concept claimed and disclosed here, the compound containing titanium can be a water-soluble titanium salt. Suitable titanium salts include, but are not limited to, titanium oxychloride, titanium sulfate, titanium oxynitrate and the like. TiO2 precipitation from water-soluble salts can be affected by adjusting the pH of the solution to a pH at which the water-soluble titanium salt will hydrolyze and form TiO2, which precipitates out of the solution. Typically, this is achieved by raising the pH of the solution with the addition of a base compound such as NaOH, for example, but not by way of limitation.
[047] The solution of the titanium-containing compound may be an aqueous solution or may comprise a suitable organic solvent added to the water to achieve hydrolysis of the titanium-containing compound. Mixtures of water and an organic solvent can also be used to control the rate of hydrolysis of the compound containing titanium and the precipitation of TiO2. If organic solvents are used, the solvents will typically be water miscible or have sufficient water solubility so that sufficient water is available to hydrolyze the titanium-containing compound to TiO2. Suitable organic solvents include alcohols, such as methanol, ethanol, isopropanol and the like; amides, such as dimethylformamide and dimethylacetamide and the like; and sulfoxides, such as dimethyl sulfoxide. There is essentially no limitation on the concentration of the solution of the titanium-containing compound, although preferably it is adequately concentrated in such a way that the kinetics of precipitation is optimized.
[048] Precipitation can be affected by any suitable method, including, without limitation, hydrolysis, pH adjustment, or solvent displacement. The precipitation method employed will be largely determined by the selection of the compound containing titanium. For example, hydrolysis is the preferred method of precipitation in which the titanium-containing compound is titanium dioxide or titanium acetylacetonate. For titanium oxychlorides or titanium sulfates, which are soluble in water, precipitation is best accomplished by adjusting the pH (for example, increasing the pH) or by adding a solvent in which the compound is practically insoluble, such as acetone or higher alcohols ("solvent displacement"). By "practically insoluble" is meant that the solubility of the titanium-containing compound is low enough in the solvent to allow titanium dioxide to precipitate out of the solution when it comes in contact with the second solvent. By "higher" alcohols is meant C5 or higher alcohols, including, without limitation, pentanol, hexanol, heptanol, octanol, for example.
[049] In one embodiment, the compound containing titanium is mixed with an alcohol. When the titanium-containing compound is hydrolyzed, it forms TiO2 which precipitates as amorphous TiO2 particles with an average particle size of less than about 50 nm. In another embodiment, the titanium-containing compound is mixed with a chelating base to form a chilled titanium species and the mixture is then added to the water to hydrolyze the titanium-containing compound and precipitate the amorphous TiO2.
[050] Any base known to those skilled in the art that will increase the pH of the water-soluble aqueous solution of the titanium salt can be used to precipitate TiO2, including inorganic and organic bases. Suitable bases include, but are not limited to, amine bases, including, ammonium hydroxide, mono-, di- or trialkylamines, such as triethylamine, diisopropylethylamine and the like; cyclic amine bases, such as N-ethyl-morpholine, piperidine, pyrrolidine and the like; hydroxides or alkoxides of alkali metals or alkaline earth elements, such as sodium, lithium, potassium hydroxide, magnesium hydroxide, calcium hydroxide; sodium, lithium or potassium, alkoxides such as methoxide, ethoxide, butoxide, t-butoxide and the like; carbonate and bicarbonate of bases, such as sodium, lithium or potassium carbonate and carbonate and bicarbonate bases, such as carbonate and sodium bicarbonate, lithium or potassium and the like. It will be apparent to those skilled in the art that the type of base is not limited to the bases described above and that there are many other bases that can be used to adjust the pH of the water-soluble titanium salt solution.
[051] Alternatively, TiO2 can be precipitated from the solution, changing the solvent composition so that TiO2 is no longer soluble. In this embodiment, a compound containing titanium which is in solution in a suitable solvent can be added to a second "anti-solvent", in which the precursor is not soluble. For example, this can be achieved by adding a compound containing titanium in a water-miscible organic solvent, such as acetone or alcohols higher than water. Alternatively, precipitation can be achieved by adding a water-miscible organic solvent to an aqueous solution of the titanium salt, soluble in water to lower the solubility of TiO2. The formed titanium precipitate can be used in the next step of the process, whether it is partially hydrolyzed or totally hydrolyzed in TiO2.
[052] In certain aspects of the invention, controlled hydrolysis or controlled precipitation of the compound containing titanium is obtained by treating the compound containing titanium a chelating agent, which forms stable chelate bonds with the titanium in aqueous solution, prior to hydrolysis titanium-containing compound and TiO2 pre-precipitation. Using the chelating agents, the rate of hydrolysis or precipitation of the titanium-containing compound in water can be controlled, thereby controlling the particle size of the formed TiO2 particles.
[053] In the presently described and claimed inventive concept (s), a neutral or basic chelating agent can be used. Suitable neutral chelating agents include dicarbonyl compounds, such as a diketone, a diester, a ketoester and the like. Diketone chelators include 2,4-pentanedione, 1,4-hexanedione, 1,3-pentanedione, 2,4-hexanedione, and dipivaloyl methane. Diester chelators include alkyl mono- or di-alkyl esters of dicarboxylic acids. Suitable diesters include dialkyl malonates, such as dimethyl and diethylmalonates and the like. Ketoester chelators include, but are not limited to, alkyl acetoacetates, such as methyl acetoacetate, ethyl acetoacetate, isopropyl acetoacetate, butyl acetoacetate and the like. Mixtures of two or more dicarbonyl chelators can also be used to prepare the inventive soles.
[054] Basic chelating agents include organic bases, which comprise two or more functional groups that are capable of chelating the titanium atom. Suitable chelating agents include dialcanolamines and trialcanolamines, such as dietanolamine, triethanolamine and the like. Other suitable chelating bases, with two or more functional groups include ethylenediamine, diethylenetriamine, triethylenetramine, 2,2'-bipyridine, 1,10-phenanthroline, ethylenediamine tetraacetic acid or tetracemate, ethylene diaminetriacetic acid or triacetate, 2,2 ', 2 "- terpiridine, 1,4,7-triazacyclononane, tris (2-aminoethyl) amine, and the like.
[055] The addition of a base chelating agent for the compound containing titanium, results in more stable species before precipitation, and can reduce the degree of hydrolysis thus facilitating the peptization of the titanium particles in the next step. In one embodiment, the base used to treat the titanium-containing compound is the same base used as an alkaline peptizing agent. The amount of chelating base added to the titanium-containing compound is such that the molar ratio of base to titanium can, in one embodiment, be <or = 0.5: 1. In another embodiment, the molar ratio of base to titanium can be <or = 0.3 or 0.2: 1.
[056] When a soluble titanium salt is used as a compound containing titanium and an organic base is used as an alkaline peptizing agent, the deionization step can alternatively be used to reduce the concentration of ions present in the compound containing titanium before the precipitation step. Lowering the ion concentration in the solution facilitates the chelation of titanium with chelating agents. Any method that will reduce the level of ions in the soluble titanium salt solution can be used, including treatment with an anion exchange resin, precipitation of insoluble salts, and the like.
[057] In one embodiment, the titanium-containing compound is treated with an anionic ion exchange resin to remove excess ions that may be in the solution of the titanium-containing compound such as sulfate ions, chloride ions, and similar, depending on the nature of the soluble titanium salt. When the soluble titanium salt solution is treated with an ion exchange resin, the pH of the solution will typically increase over time and may result in the formation of a TiO2 precipitate. Preferably, the treatment time of the soluble titanium salt with an anion exchange resin will be limited, so that the pH of the solution is maintained at less than about 3, in order to avoid the formation of a precipitated TiO2. Most preferably, the deionization treatment will be limited so that the pH of the solution is maintained at less than about 2. Once the ion level is reduced, the titanium salt solution is separated from the ion exchange resin and treated with a base that is capable of forming a chelating bridge, as described above. The pH of the solution of the chelate titanium dioxide salt is then adjusted with a suitable base to form TiO2 which precipitates out of the solution.
[058] The precipitated TiO2 can be collected by any suitable means, including decantation, centrifugation and filtration. The isolated solid can optionally be washed with water to remove the by-products of the hydrolysis reaction and other impurities, before the dispersion step in a liquid medium.
[059] In one embodiment, the precipitated TiO2, which is in an amorphous form, is generally collected by filtration and carefully washed with deionized water before further dispersion. The washed wet filter cake is then dispersed again in a volume of deionized water with vigorous stirring (eg, stirring with a deep vortex, stirring, etc.) Deionized water usually, although not always, comprises peptizing agents alkalis in solution before the dispersion is formed. Since the benefit of the alkaline peptizing agent is largely realized during the subsequent heat treatment step, it is not strictly necessary that the alkaline peptizing agent is present in the aqueous solution, before the precipitate is dispersed again. Instead, the alkaline peptizing agent can still be added after the dispersion is formed, or it can be added to the compound containing titanium before precipitation is carried out, or it can be added during or along each or both steps. The amount of deionized water used will be such that the weight ratio of the initial titanium-containing compound (eg, titanium isopropoxide) to the total weight of the dispersion is about 1: 2 to about 1:10, about 1: 3 to about 1: 6, and from about 1: 4 to about 1: 5.
[060] The concentration of TiO2 in the dispersing liquid determines the initial concentration of the sun after peptization. TiO2 soles can be further diluted or concentrated, if desired, after the peptization step is complete. Typically, a dispersion of TiO2 from about 1% to about 30% of TiO2, by weight, in an aqueous solvent will be used for the peptization step. The aqueous solvent can be any solvent or solvent mixture comprising water. For example, mixtures of water and a water-miscible solvent, such as an alcohol, can be used. More typically, the concentration of the dispersion is about 2% to about 15% or about 5% to about 15% by weight of the mixture. In one embodiment, the concentration is about 8% to about 12% or about 5% to about 10% by weight.
[061] The precipitated TiO2 is then treated with an alkaline peptizing agent with agitation to form the TiO2 soles of the inventive concepts currently claimed and described. The dispersed TiO2 can be treated with the alkaline peptizing agent at room temperature or at a selected high temperature or temperature range, with stirring until the dispersion forms a transparent or translucent mixture. A wide variety of alkaline peptizing agents can be used in the inventive concept (s) presently described and claimed. The alkaline peptizing agents used here, with respect to this step, are the same as those previously described.
[062] Peptization is typically carried out at a temperature of about 70 C to about 150 ° C (ie, a heat treatment) for a period of time from about 3 hours to about 3 days, with continuous agitation or intermittent. It is not necessary to neutralize the solution before any heat treatment. Therefore, in an embodiment, the dispersion comprising the alkaline peptizing agent is not subject to a neutralization step, such as by adding a base solution, before or during the heat treatment. It has also been found to be useful, in one embodiment, for carrying out the peptization in a closed hydrothermal reactor, due to the concomitant increase in pressure. Hydrothermal pump-type reactors, such as those available from Parr Instruments (Illinois), have been found suitable for use in the hydrothermal reaction, for example, but not by way of limitation. One or more pump reactors can be placed in a cylinder oven or similar, to provide thermal conditions and acquire agitation. The resulting alkaline colloidal suspension of titanium dioxide can be neutralized by boiling the sun, mixing hydrogen peroxide with the colloidal suspension, or mixing an acidic compound with the sun. All of these neutralization methods are the same as those previously described.
[063] In accordance with another embodiment of the invention, a colloidal suspension of neutral, stable and transparent photocatalytic titanium dioxide can be formed from a colloidal suspension of alkaline titanium dioxide, which is peptized and neutralized. The titanium dioxide sol can be peptized with an alkaline peptizing agent as described above, thus forming a colloidal suspension of peptized alkaline titanium dioxide, which can be neutralized by an acidic compound as described above, thus forming the sol of neutral, stable and transparent photocatalytic titanium dioxide.
[064] The neutral, stable, transparent or translucent TiO2 soles can contain from about 0.5% to about 40% of TiO2, by weight, of an aqueous solvent. More typically, soles can contain from about 2% to about 20% or from about 2% to about 15%, or between about 5% to about 20%, or between about 5% to about 15% titanium dioxide by weight. In one embodiment, the soles can contain between about 8% to about 12% or about 5% to about 10% TiO2 by weight of the mixture. According to another embodiment, neutral, stable, transparent or translucent TiO2 soles can contain from about 20% to about 40%, or between about 25% to about 40%, or between about 30 % to about 40% titanium dioxide by weight.
[065] TiO2neutral, stable, transparent or translucent soles can contain at least about 10% or at least 15% or at least 16% or at least 17% or at least 18% or from about 10% to about 20% or from about 12% to about 16% or at least 16% to about 18% alkaline peptide based on the combined weight of the alkaline peptide and TiO2.
[066] When the alkaline peptizing agent is present in neutral, stable, transparent or translucent TiO2 soles, in an amount of at least about 7% based on the combined weight of the alkaline peptizing agent and TiO2, the resulting sol of peptized alkaline titanium dioxide can be neutralized with an acid comprising phosphoric acid. In addition, neutral, stable, transparent or translucent TiO2 soles can contain from about 5 to about 20 or about 30 to about 40% by weight of titanium dioxide.
[067] When the alkaline peptizing agent is present in the neutral, stable, transparent or translucent TiO2 soles in an amount of at least about 18% based on the combined weight of the alkaline peptizing agent and the TiO2, the sol de The resulting peptized alkaline titanium dioxide can be neutralized with a combination of phosphoric acid and acetic acid; wherein the weight ratio of phosphoric acid to acetic acid can range from about 0.8: 1 to about 1.2: 1, or from about 0.9 to about 1.1 or about 1: 1. Phosphoric acid and acetic acid can be substantially and simultaneously added to the peptized alkaline titanium dioxide sol. In addition, neutral, stable, transparent or translucent TiO2 soles can contain from about 5 to about 20 or from about 30 to about 40% by weight of titanium dioxide.
[068] The peptide alkaline titanium dioxide sol or the neutral, stable and transparent photocatalytic titanium dioxide sol can also be washed with demineralized water in such a way that the concentration of calcium ions and sodium ions is less than about 71 ppm , and less than about 13 ppm, respectively, in the resulting washed material. The conductivity of the resulting filtrate can be 500 μS or less. The viscosity of the resulting washed peptized alkaline titanium dioxide sol or the neutral, stable, transparent photocatalytic titanium dioxide sol can be less than about 100 centipoise after at least 4 weeks at room temperature.
[069] Neutral, stable and transparent photocatalytic titanium dioxide soles are reactive, stable and transparent, over a pH range of about 7 to about 9.5. The average particle size of the photocallitic titanium dioxide sol, neutral, stable and transparent after neutralization will generally be less than about 50 nm, although one skilled in the art will appreciate that some amount of the process may have a particle size > that about 50 nm without affecting the inventive concept claimed here and disclosed described. More typically, the average particle size of the titanium dioxide particles will be less than about 30 nm, 20 nm or 10 nm. In one embodiment, the crystallite size of the titanium dioxide sol will be less than about 5 nm. References made here to the size of titanium dioxide particles will be understood to mean the mean particle size of titanium dioxide particulates. When the particle size is modified by the term "about," (and as the term is used elsewhere) it will be understood in the scope, both larger and smaller in particle sizes than the value indicated to account for experimental errors inherent in the measurement and variability between different methodologies for measuring particle size (or temperature, pressure, pH or time, for example), as will be evident to a person skilled in the art. Diameters can be measured by conventional particle size analysis techniques, for example, transmission electron microscopy (TE, XRD) or by light scattering techniques (for example, without limitation, dynamic light scattering, by Malvern Instruments Ltd ., UK).
[070] Alternatively, the particles can be characterized by the surface area. Typically, the titanium dioxide used in the soles of the inventive concept presently claimed and described will have a surface area, as measured by any suitable method, including 5-point BET in a dry sample, or greater than about 20 m2 / g. More typically, photocatalytic titanium dioxide particles have surface areas greater than about 50 m2 / g or greater than about 70 m2 / g. In one embodiment, the titanium dioxide particles have surface areas greater than about 100 m2 / g. In another embodiment, the surface areas are greater than about 150 m2 / g. In yet another embodiment, the titanium dioxide particles will have a surface area greater than about 200 m2 / g, greater than about 250 m2 / g, or greater than about 300 m2 / g.
[071] Colloidal solutions according to the inventive concepts currently claimed and described can optionally include additional ingredients, provided that the addition of such ingredients does not have a negative impact on either the transparency or the stability of the sun. For example, it is considered that colloidal solutions may include minor amounts of bactericidal agents, organic solvents (for example, alcohols), film-forming aids, drying agents, pH regulators, without limitation. In one embodiment, the soles will be substantially free of metal ions chosen from the group l-VA, and series of lanthanides or actinides from the periodic table, so it is understood that there are no additional amounts of such metal ions added to the soles or intermediate preparations , in addition to any traces that are present as impurities in the titanium starting material or other reagents.
[072] Because the soles according to the inventive concepts currently claimed and described are transparent, it has also been advantageously found that the colloidal solutions form films that, when applied to a substrate, are also transparent. Included in the inventive concept presently claimed and described there is, therefore, a method of forming a transparent, photocatalytic (o) self-cleaning film or coating on a substrate, by applying to the substrate, the colloidal solutions according to inventive concepts presently claimed and described. Generally, the films are allowed to dry on the substrate, forming a transparent coating having adequate adhesion to the substrate for use in the particular application or the medium for which it is intended. There is essentially no limit as to the nature of the substrate to which the colloidal solutions of the presently claimed and described inventive concept can be applied. Cement, metal, glass, polymer, wood, ceramics, paper, textiles, and leather substrates are each considered suitable, for example, but not by way of limitation.
[073] The stable, transparent colloidal solutions of the inventive concept claimed and disclosed here will find special use in any application where photocatalytic activity is desired. Due to the transparent nature of the soles, they are ideal for coating surfaces or structures that are themselves transparent (i.e., glass), or to provide a coating that does not alter the appearance of the underlying substrate. Notable applications include, without limitation, photocatalytic coatings for the clean-up of air on road surfaces, floors and ceramic tiles, building exteriors, window glass, automobile windshields and the like. The soles of the inventive concept claimed and disclosed here will also find use in fabrics, furniture, works of art, for example, due to their self-cleaning properties. This activity also provides substitutes treated with the soles of the inventive concept presently claimed and disclosed with a “stainless” or “stain free” or “stain repellent” character. In addition, the soles of the inventive concept claimed and disclosed here also provide protection against ultraviolet rays to the substrates they are applied in. In a particular embodiment, for example, but not by way of limitation, the colloidal solutions of the inventive concepts presently claimed and described can be coated on clothing or other items susceptible to to be worn out or disposed of in a mammal like a human being. The clothing with the soles coated on it would thereby effectively block the X-rays emitted from reaching through the clothing and interact with the bodily tissues. protective clothing or curtains can be worn by an X-ray technician or lab technician and subsequently provide a level of protection against X-rays or other UV radiation.
[074] In addition, a layered structure containing titanium dioxide may comprise a substrate and a layer containing titanium dioxide in the form of substantially anatase on the substrate surface, where the transparency of the The layer containing titanium dioxide at a wavelength of visible light of 400-700 nm can be from about 65% to about 95% and the layer containing titanium dioxide can be formed from the colloidal titanium dioxide suspension. neutral, stable and transparent photocatalytic described above. The thickness of the layer containing titanium dioxide can be about 0.1-1.5 μm. The structure can also show an initial amount of NOx removal from the air in the vicinity of the layer containing titanium dioxide of at least about 80%, or at least about 75% after about 450 days.
[075] The stable, transparent titanium dioxide sol of the claimed and described concept of the present invention has a photocatalytic effect, which also has redox functionality and thus is able to decompose harmful components and also provides antibacterial properties to the coated substrate when irradiated with lights, such as sunlight and / or an ultraviolet light source. Thus, the coatings containing the stable and transparent titanium dioxide soles of the inventive concept claimed here and disclosed or the substrates coated with these soles have antibacterial properties. In addition, these colloidal solutions confer a deodorizing effect and are capable of reducing harmful fumes in the area adjacent to the soles or substrates coated with these colloidal solutions.
[076] According to another embodiment, an antibacterial composition can comprise any of the neutral, stable and transparent photocatalytic titanium dioxide soles described herein; where the antibacterial composition, when placed in contact with the bacteria, can kill at least 80% or at least 90% of these bacteria. The antibacterial composition can be used as a partial or complete coating of a device, such as, but not limited to, a medical device. In addition, the photocatalytic antibacterial activity of the antibacterial composition, when placed in contact with the bacteria, is at least about 2 or at least about 3; in which the photocatalytic antibacterial activity is determined according to the formula: log (BL / CL) - log (BD / CD); and where BL = average bacterial count on a control surface not coated with the antibacterial composition after X hours of exposure to light; CL = average bacterial count on a test surface coated with the antibacterial composition after X hours of exposure to light; BD = average bacterial count on a control surface not coated with the antibacterial composition after X hours in the dark; CD = average bacterial count on a test surface coated with the antibacterial composition after X hours of darkness; and X ranges from about 14 to about 24 hours.
[077] The photocatalytic coating based on the colloidal solution of the currently claimed and described concept of the invention can also be doped with a metal to kill bacteria adhered to the surface. Metal, for example, but not by way of limitation, is selected from the group consisting of Ag, Zn, Mg, Sn, Fe, Co, Ni, Se, Ce, Cu and their combinations. The doping of the photocatalytic coating with the metal can be carried out by adding a soluble salt of the metal to the colloidal titanium solution. The metal salt can be a nitrate, a sulfate or a chloride, for example, but not by way of limitation. The amount of metal salt added is generally from about 0.01% to about 1% of the titanium compound per molar amount, although a person skilled in the art will understand that, greater amounts can be used, depending on the use for which the sun or the photocatalytic coating is intended. The resulting solution, which the doped metal can be used, forms the photocatalytic coating (s) described above. In one embodiment, for example, photocatalytic coatings of the inventive concept (s) presently claimed and described (with or without doping metal) inhibit and / or are resistant to colonization of methicillin-resistant Staphylococcus aureus (MRSA).
[078] Alternatively, after the photocatalytic coating is formed, a soluble salt of the metal can be applied over it and the resulting coating can then be subjected to irradiation or light emission in order to deposit the metal by photo. -reduction. The photocatalytic coating of contaminated metal is capable of killing bacteria attached to the surface. In addition, this photocatalytic coating of doped metal can further inhibit the growth of microorganisms, such as mold, algae and moss, for example, but not by way of limitation. As a result, the surface of a building, a machine, a household appliance, article and the like can be kept clean, substantially without bacterial colonization for an extended period of time. As such, the soles of the inventive concept claimed and disclosed here have commercial applicability for the restoration of construction and medical industries, for example, but not by way of limitation. EXAMPLES
[079] The following examples are presented to assist in understanding the inventive concept presently claimed and described, not intending and not to be interpreted in a way that limits the inventive concept claimed and disclosed in any way. All alternatives, modifications and equivalents that become evident to those skilled in the art after reading this disclosure are included within the spirit and scope of the inventive concept presently claimed and described, and should be considered as expressly included here. Example 1
[080] 200 g of non-neutralized titania sol with the product name CristalACTivTM manufactured by Cristal Global (where titania had a weight of 17.5% ± 2.5 at a pH of 11.5 ± 1) and diethylamine as an alkaline peptizing agent they were placed in a mixing bowl with baffles and stirred using a rotor mixer, to provide movement and agitation throughout the volume. The pH probe was positioned to provide readings of the mixed solution. Mixtures of 5M phosphoric acid and 5M acetic acid were prepared. 100 g of each acid mixture were produced and labeled according to% (by mass) of the amount of 5M phosphoric acid in the mixture as shown in Table 1.Table 1 - Acid Compositions


[081] The acid mixture was added at a substantially constant rate (about 0.5-0.7 g / min) equivalent to 0.25-0.35% of the mass of the sun per minute. The addition of acid was slowed when a pH value of about 9.0 was reached in order to obtain a final pH of 8.5. When the pH = 8.5 was obtained, the addition of acid was stopped, and the mixing continued for at least about 60 minutes. During this time the pH increased slightly to approximately 8.7-8.9 Thus, small additions of acid were made when necessary in order to adjust the pH back to 8.5. About 5.5% of the acid mixture was added, based on the weight of the colloidal alkaline titanium dioxide suspension. The titanium dioxide content was about 15% by weight and the diethylamine content was about 2.5% by weight, each based on the total weight of the colloidal neutralized titanium dioxide suspension. The viscosity of the neutralized colloidal titanium dioxide suspension was measured to be about 18 cps. The surface area, measured by BET, of a product sample, subsequently dried, was 250 m2 / g. Example 2
[082] In order to investigate the photocatalytic activity of coatings prepared from soles according to the inventive concept presently claimed and described, the neutralized soles of Example 1, as well as a titanium dioxide sol prepared in a similar manner to from Example 1, but containing tetra-methylammonium hydroxide (TMAOH) instead of diethylamine, which were each neutralized with various mixtures of phosphoric and acetic acid (as described in Table 1), were deposited on test strips of 15 mm x100mm cut from Whatman 541 filter paper. About 0.05 g to about 0.0520 g of neutralized soles in areas of about 5 to about 5.2 g / m2, was added for each test strip. Each test strip was dried for 24 hours before testing with NOx The methodology for determining NOX reduction was substantially as described in US Patent Publication 2007/0167551, the description of which is hereby incorporated by reference in its entirety. Briefly, the test samples were placed in an airtight sample chamber and sealed. The sample chamber was in communication with a three-channel gas mixer (Brooks Instrument, Holland) through which NO (nitrogen oxide), NO2 (nitrogen dioxide), and compressed air containing water vapor were introduced. in the chamber at predetermined levels. The test samples were irradiated with 6.2 W / m2 / m of UV radiation in the range of 300 to 400 nm from a Model VL-6LM UV lamp with 365 & 312 nanometer wavelengths (BDH). The initial values and the final values (after five minutes of irradiation) of NOx were measured by a ML9841 B Nitrogen Oxide Analyzer Model (Europe Monitor), connected to the sample chamber. The% NOx reduction was measured as (ΔNOX / initial NOx) x100. The results of these tests are shown and described in Figures 1 and 2.
[083] The results of the examples indicate that the colloidal solutions of neutralized titanium dioxide exhibit a greater NOx-lowering activity than that of the original non-neutralized alkaline titanium dioxide sol. In most cases, NOx reduction activities are increased when the proportion of phosphoric acid added to the alkaline titanium dioxide sol is increased.
[084] NOx removal has also been studied under different lighting and source conditions. In addition to UV light, low intensity fluorescent strip lighting and visible light (as filtered through glass) were employed. Figures 3 and 4 show and describe the% NOx reduction achieved using each of these different light sources. The results indicate that the neutralized titanium dioxide sol has greater NOx-reducing activity than the original non-neutralized alkaline titanium dioxide sol in all different light sources. Example 3
[085] In order to investigate the photocatalytic activity of coatings prepared from soles in accordance with the concept of the invention presently claimed and described, titanium dioxide soles were prepared in the same way as Example 1, but instead of treatment with the phosphoric acid / acetic acid mixture of Example 1, these colloidal titanium dioxide solutions were treated with the following acid mixtures: oxalic acid / nitric acid, oxalic acid / acetic acid, citric acid / nitric acid, citric acid / nitric acid, phosphoric acid / nitric acid, and phosphoric acid / acetic acid, respectively. For individual soles, either 1M oxalic acid or 1M citric acid or 1M phosphoric acid was added in an amount of 0.1% by weight based on the total weight of the sun; by adjusting the pH of the soles to 8.5 by adding, either nitric acid or acetic acid. These acid-treated soles were deposited as thin layers on concrete substrates (about 0.3 ml of sun in an area of 18 cm2). Activity against NOx pollutants under UV radiation (6.2W / m2) was measured at various intervals over a period of about 288 days (activities for oxalic acid / acetic acid and phosphoric acid / acetic acid soles were measured over the complete period of 288 days; while the period for measuring the activity of the remaining soles was up to 120 days). The methodology for determining NOX reduction was substantially as described in U.S. Patent Pub. 2007/0167551, the description of which is hereby incorporated by reference. The results of these tests are shown and described in Figure 5. Example 4
[086] In order to investigate the photocatalytic activity of coatings prepared from soles in accordance with the concepts of the invention presently claimed and developed, titanium dioxide soles from Example 3 above were also deposited as layers thin on glass substrates (about 0.3 ml of sun in an area of 18 cm2). Activity against NOx pollutants under UV radiation (2 W / m2) was measured at various intervals over a period of about 288 days (activities for soils treated with oxalic acid / acetic acid and phosphoric acid / acetic acid were measured at over a complete period of 288 days, while the period for measuring activity for the remaining soles was up to 120 days). The methodology for determining NOX reduction was substantially as described in U.S. Patent Pub. 2007/0167551, the disclosure of which is hereby incorporated by reference. The results of these tests are shown and described in Figure 6. Example 5
[087] In order to investigate the photocatalytic activity of coatings prepared from soles according to the concepts of the invention presently claimed and developed, the neutralized titanium dioxide sol of Example 1 (having a ratio of 1: 1 by weight of phosphoric acid to acetic acid) was deposited in thin layers on concrete (about 0.3 ml of 10% titanium oxide sol in an area of 18 cm2). The thin layers on the concrete were exposed separately, to 225 ppb of NO, 225 ppb of NO2, 70 ppb of NO and 70 ppb of NO2, respectively. Activity against NOx pollutants under UV radiation (6.23 W / m2, 295-400 nm) was measured at various intervals over a period of about 1000 days. The methodology for determining NOX reduction was substantially as described in U.S. Patent Pub 2007/0167551, the disclosure of which is hereby incorporated by reference herein. The results of these tests are shown and described in Figure 7. Example 6
[088] In order to investigate the photocatalytic activity of coatings prepared from soles in accordance with the concepts of the invention presently claimed and described, a thin layer of the colloidal suspension of the neutralized titanium oxide of Example 1 ( with a 1: 1 ratio by weight of phosphoric acid to acetic acid), which was diluted with water to form a colloidal suspension at 10% by weight of titanium dioxide sol, was coated on a concrete wall (about 16L of titanium dioxide sol 10% by weight in an area of 135 m2) located in an area of Camden London, England. (GPS coordinates of 51.518904 N and 0120685 W). The air quality in the area was above UK air quality standards at the site, at the start and end of the test. NO and NO2, together with wind speed, wind direction, temperature and humidity were measured at 15-minute intervals. NO and NO2 were measured in a probe at a distance of 15 cm from the wall. Figures 8 and 9 show comparisons of the amounts of NO and NO2 at the baseline with those measured on the concrete wall coated with a colloidal suspension of peptized alkaline titanium dioxide. The comparisons show the averages of the quantities of NO and NO2, measured at each hour of the day, for each day of the week, over more than 2 years. The comparisons also include only the NO and NO2 data, where the wind speed was less than 1.3 m / s. The titanium dioxide sol maintained a high NOx removal activity, even after exposure for more than two years to the environment with high levels of NO and NO2 in the atmosphere involving the substrate coated with the titania sols of the currently claimed concepts of the invention and described. Example 7
[089] In order to investigate the antibacterial activity of the prepared coatings of the soles according to the concepts of the invention presently claimed and revealed, samples of the colloidal suspension of neutralized titania of Example 1 (with a 1: 1 ratio by weight of acid phosphoric to acetic acid) were doped with Ag or Zn as mentioned in Table 2. Samples B, C and D were diluted in such a way that the weight of titanium dioxide was 10%. Table 2 - Used titanium dioxide soles in Antibacterial Activity Tests

[090] The doped and non-doped titanium dioxide soles were coated on glass slides to test the antibacterial activity against Staphylococcus au-reus. The test for antibacterial activity (due to photoactivity) was carried out using a procedure based on the standard number BS ISO 27447: 2009 promulgated by ISO, which specifies a test method to determine the antibacterial activity of materials containing a photocatalyst or having photocatalytic films on its surface. The method described above was used to measure the bacteria count under UV light irradiation. The standard was based on the ISO 22196: 2007 standard number (formally JIS Z 2801: 2000). Generally, however, antibacterial activity was measured by quantifying the survival of bacterial cells, which were kept in close contact for 24 hours at 21 ° C, with a surface containing an antibacterial agent. The antibacterial effect was measured by comparing the survival of the bacteria in a treated material with that obtained in an untreated material.
[091] The titania soles in Table 2 were applied to glass slides for testing. Some minor changes in certain parts of the method were necessary due to the hydrophobic character of the materials. The samples were tested in duplicate against a set of controls. A known amount of Staphylococcus aureus suspension, (- ie 0.05 ml of a suspension of the test organism (adjusted to contain about 5 x 105 cells in 0.05 ml)) - was applied to the coated slides (coated samples ) and on a "white" slide (known to have no microbial activity and used as a control sample). The suspension was kept in contact with three identical coated samples and 6 replicates of control samples. The three identical coated samples and 3 of the 6 replicates of control samples were then incubated for 24 hours at 21 ° C and relative humidity not less than 90%. After incubation, the samples were transferred to individual containers containing 10 ml of sterile neutralizing solution. The three replicates of control samples were also processed in this manner, prior to incubation, to provide reference or control data. The replicas of each of the surfaces coated with a solution of titanium dioxide sol were exposed to light (daylight, fluorescent), while the others were placed in the dark. After these steps, bacterial counts were determined. The bacterial counts obtained (shown as a geometric mean), together with antibacterial activities (shown as a reduction of Log10) are shown in Table 3.
[092] The antibacterial activity after exposure to light was calculated as follows: RL = log (BL / A) - log (CL / A) = log (BL / CL)
[0093] Antibacterial activity in the dark was calculated as follows: RD = log (BD / A) - log (CD A) = log (BD / CD)
[0094] The photocatalytic antibacterial activity was calculated as follows: RP = log (BL / CL) - log (BD / CD) where, RL is the antibacterial activity after exposure to light RD is the antibacterial activity in the dark RP is the photocatalytic antibacterial activity A = average bacterial count in a control sample at zero time BL = average bacterial count in a control sample after 14 hours of exposure to light (+ 10 hours in the dark) CL = average bacterial count in a test piece after 14 hours of exposure to light (+10 hours of darkness) BD = average bacterial count of a control sample after 24 hours of darkness CD = average bacterial count in a test piece after 24 hours of darkness Table 3 = Activity Test Results Antibacterial

[095] Since the accepted / failure criterion is not defined in the standard, the following criterion (as shown in Table 4) was used to comment on the determined activity level.Table 4 - Classification of Antibacterial Activity


[096] The test results indicate that all titania sols of the inventive concepts currently claimed and disclosed (whether doped or not doped with a metal) demonstrate excellent antibacterial activities after exposure to daytime fluorescent lamps. Example 8
[0097] A first colloidal suspension which is a neutralized titanium dioxide sol from Example 1 (with a 1: 1 ratio by weight of phosphoric acid to acetic acid, which has been diluted to 10% by weight of TiO2, 15% by weight) and a second colloidal suspension (made from a different precursor and having a concentration of TiO2 between 0.5 and 2.0%) were used to test the antibacterial activity against MRSA (methicillin-resistant Staphylococcus aureus) . Table 5 shows the compositions of the tested samples. Table 5 - Samples for Testing Antibacterial Activity against MRSA

[098] The assay for antibacterial activity (due to photoactivity) was performed using a procedure based on the BS ISO 27447: 2009 standard number, which specifies a test method to determine the antibacterial activity of materials containing a photocatalyst or having photocatalytic films on the surface. The method was used to measure the bacterial count under UV light irradiation. The standard was established in the ISO 22196: 2007 standard number (formally J IS Z 2801: 2000).
[099] The coated panels (Samples 1 and 2) were each cut into test pieces measuring about 35 mm x 35 mm. The test was performed using Sta-phylococcus aureus ATCC 43300 (MRSA). For each test sample 0.1 ml of a suspension of the test organism (adjusted to contain about 5 x 105 cells in 0.1 ml) was placed on the coated surface of each of the 6 replicates and in 6 replicates of glass (used as controls and known to have no antibacterial activity). The suspension was maintained in close contact with the test and control surfaces, using glass coverslips with dimensions of 20mm x 20 mm. In order to provide a zero time inoculation level, an additional triplicate set of control samples was inoculated and washed immediately, each in 10 ml of neutralized sterile solution and microbial counts were determined to give a count in zero time.
[0100] For each set of six replicates, 3 were exposed on a glass test plate, for 14 hours of the 24 hours under daytime fluorescent lamps. The test plate containing the remaining three replicates of each test and control sample was wrapped in several layers of black plastic to prevent any light from reaching the test films. This assay plate remained in the dark for 24 hours. The incubation for both sets of samples was 21 ° C and the relative humidity was not less than 90%. After this time, the test pieces were washed, each in 10 ml of sterile distilled water, with a bacterial count.
[0101] Samples 3-5 were tested using Staphylococcus aureus ATCC 43300 (MRSA). Due to the hydrophilic nature of the coated surfaces (which increased with increasing concentration of TiO2), the method used previously was modified. A volume of inoculum of 0.1 ml, which is normally used, has been seen to spread too much in sample C and cannot be "stuck" under the coverslip. A volume of 0.05 ml was used in place, as this is considered the best fit for use on all three surfaces.
[0102] A quantity of 0.05 ml of a suspension of the test organism (adjusted to contain about 5 x 105 cells in 0.05 ml) was placed on the coated surface of each of the 6 replicates of test samples and 6 replicates of glass slides (used as controls and known to have no antibacterial activity). The suspension was kept in close contact with the test and control surfaces, using 20 mm x 20 mm glass coverslips. In order to provide a zero time inoculation level, an additional triplicate set of control samples were inoculated (again using a 0.05 ml inoculum volume), washing immediately, each in 10 ml of sterile neutralizing solution , determining microbial counts to give a count in zero time.
[0103] As previously described, three replicates of each coated slide plus three controls were exposed to light and three replicates of each coated slide plus three controls were placed in the dark, after which, bacterial counts were determined. The bacterial counts obtained (shown as a geometric mean), together with antibacterial activities (shown as reduction of Log10), are given in Tables 6 (coated panel) and 7 (Coated Glass Laminates). The calculations of antibacterial activity and photocatalytic antibacterial activity are the same as those described in Example 7.Table 6 - Results of the Antibacterial Activity Test: Coated Panel
Table 7 - Results of the Antibacterial Activity Test - Coated Glass Blades


[0104] The criterion for analyzing the level of antibacterial activity is the same as that listed in Table 4 of Example 7. Referring to Table 6, PCX-S7 in paint / panel Q demonstrated good antibacterial activity when exposed to light , but the activity was very weak in the darkness. Overall, good catalytic activity has been demonstrated. Stainless steel PCX-S7 demonstrated excellent antibacterial activity when exposed to light and good activity in the dark. Overall, good photocatalytic activity against MRSA has been demonstrated.
[0105] Referring to Table 7, Samples A and B (PCX-S2) demonstrated a good borderline antibacterial activity when exposed to light, but weak catalytic activity in the dark. In general, borderline photocatalytic activity against MRSA has been demonstrated. Sample C (PCX-S7 on glass), however, demonstrated excellent antibacterial activity when exposed to light, but weak activity in the dark. Overall, excellent photocatalytic activity against MRSA has been demonstrated. Example 9
[0106] Six ink samples and four sun samples (Soles 1 to 4) were tested for antibacterial activity against Staphylococcus aureus. The ink samples, labeled 1 to 6, contained different TiO2 photocatalysts and were applied to aluminum Q panels being prepared using the phosphoric acid / acetic acid sol in the 1: 1 weight ratio of Example 1. The samples of the sun, labeled 1 to 4, were colloidal dispersions, prepared in the same way as the soles of Example 1, being applied to glass slides with TiO2 charges of approximately 0.75, 2.5, 5.0 and 11 g / m2, respectively.
[0107] The test for antibacterial activity (due to photoactivity) was carried out using a procedure based on the BS number of ISO 27447: 2009, which specifies a test method to determine the antibacterial activity of materials containing a photocatalyst or having photocatalytic films on the surface. The method was used to measure the bacterial count under UV light irradiation. The standard was based on the ISO 22196: 2007 standard number (formally JIS Z 2801: 2000).
[0108] The panels coated with paint were each cut into test pieces measuring about 35 mm x 35 mm. The test was performed using Staphylococcus aureus ATCC 6538. A quantity of 0.1 ml of a suspension of the test organism (adjusted to contain approximately 5 x 105 cells in 0.1 ml) was placed on the ink-coated surface of each of the six replicates of test samples and in replicas on glass slides (used as controls, knowing that they have no antibacterial activity). The suspension was maintained in close contact with the test and control surfaces, using 20 mm x 20 mm glass coverslips. In order to provide a zero time inoculation level, an additional triplicate set of control samples were inoculated and washed immediately, each in 10 ml of sterile neutralizing solution, and microbial counts were determined to provide zero count time .
[0109] Of the 6 replicates of each sample, 3 were exposed on a glass test plate for 14 hours out of the total 24 hours under fluorescent lamps that mimic daylight. The assay plate containing the remaining three replicates of each test sample was wrapped in several layers of black plastic to prevent any light from reaching the test films. This assay plate remained in the dark for the total 24 hours. The incubation for both sets of samples was done at 21 ° C and relative humidity not less than 90%. After this time, the test pieces were washed, each in 10 ml of sterile distilled water, and bacterial counts were determined.
[0110] The glass slides coated with the titanium dioxide sol were tested using Staphylococcus aureus ATCC 6538. Due to the hydrophilic nature of the titania sol coatings (which expanded with increasing TiO2 concentration), the method used above it was modified. A volume of inoculum of 0.1 ml, which is normally used, has been seen to spread too much in Sol 4 and cannot be "stuck" under the cover slip; A volume of 0.05 ml was used instead of that, being considered the best fit for use on all four sun surfaces. A 0.05 ml quantity of a test organism suspension (adjusted to contain approximately 5 x 10 5 cells in 0.05 ml) was placed on the coated surface of each of the 6 replicates of test samples and on slide replicas. glass (used as a control, knowing that they have no antibacterial activity). The suspension was maintained in close contact with the test and control surfaces, using glass slides 20 mm x 20 mm in dimension.
[0111] In order to provide a zero time inoculation level, an additional triplicate set of control samples were inoculated (again using a 0.05 ml inoculum volume) washing immediately, each in 10 ml of sterile, neutralizing solution, determining microbial counts to give zero counting time. As previously described, the replicas of each titanium dioxide sun surface were exposed to light and 3 were placed in the dark, after which, bacterial counts were determined.
[0112] The bacterial counts obtained (shown as a geo-metric mean), together with antibacterial activities (shown as the reduction of Log10), are shown in Tables 8 to 10. Calculations of antibacterial activity and antibacterial activity photocatalytic tests are the same as those described in Example 7.Table 8 - Antibacterial Activity Test Results Paints 1 to 3
Table 9 - Results of the Antibacterial Activity Test: Paints 4 to 6
Table 10 - Results of the Antibacterial Activity Test: Soles (SA)

[0113] The criterion for analyzing the level of antibacterial activity is the same as that listed in Table 4 in Example 8 above. Referring to Tables 8 and 9, the coated panel showed only very weak activity against S. aureus, both in the dark and, after exposure to fluorescent lamps imitating daylight, therefore, significant photocatalytic antibacterial activity has not been demonstrated.
[0114] Referring to Table 10, all four sun samples, however, demonstrated excellent antibacterial activity after exposure to daylight fluorescent lamps. Soles 1 to 3 clearly demonstrate excellent photocatalytic antibacterial activity. The level of photocatalytic activity of sun 4 was considered to be minimally good, although the actual level of photocatalytic activity could not be determined because this sample also demonstrated some antibacterial activity in the absence of light. Example 10
[0115] In order to investigate the stability of coatings prepared from soles according to the inventive concept presently claimed and described, titanium dioxide soles were prepared in the same way as in Example 1, but with the following differences. Two soles were prepared without neutralization and contained 34% by weight of titanium dioxide and 15% by weight and 18% by weight of diethylamine, respectively. Figure 10 is a graph of viscosity over time for these non-neutralized colloidal solutions, and shows that using 18% by weight of diethylamine results in improved stability compared to the sun containing only 15% by weight of diethylamine.
[0116] Four additional soles were prepared, which also contained 34% by weight of titanium dioxide, and underwent neutralization. The first neutralized sol contained 15% by weight of diethylamine and was neutralized with a 1: 1 ratio of phosphoric acid to acetic acid. The second neutralized sol contained 15% by weight of diethylamine and was neutralized with 100% by weight phosphoric acid. The third neutralized sol contained 18% by weight of diethylamine and was neutralized with a 1: 1 ratio by weight of phosphoric acid to acetic acid. The fourth neutralized sol contained 18% by weight of diethylamine and was neutralized with 100% by weight phosphoric acid. Each of the colloidal suspensions was also washed with demineralized water. Figure 11 is a graph of viscosity over time for these neutralized soles. Figure 11 shows that the stability is greatly increased by 15% by weight of diethylamine with neutralization using 100% by weight of phosphoric acid in relation to neutralization with a 1: 1 weight ratio of phosphoric acid to acetic acid. Figure 11 also shows that soles containing 18% by weight of diethylamine are more stable than soles containing 15% by weight of diethylamine, and that sol containing 18% by weight of diethylamine and neutralized with phosphoric acid at 100% by weight is the most stable colloidal suspension. Example 11
[0117] In order to investigate the stability of coatings prepared from soles according to the inventive concept presently claimed and described, four colloidal titanium dioxide solutions were prepared in the same way as in Example 1, but with the following differences: The four soles contained 34% by weight of titanium dioxide, and were not neutralized. The first sol contained 15% by weight of diethylamine and was washed with demineralized water, resulting in a calcium content of 71 ppm and a sodium content of less than 13 ppm. The second sol contained 18% by weight of diethylamine and was also washed with demineralized water, resulting in a calcium content of 71 ppm and a sodium content of less than 13 ppm. The third sol contained 15% by weight of diethylamine and was washed with running water, resulting in a calcium content of 2535 ppm and a sodium content of 23 ppm. The fourth sol contained 18% by weight of diethylamine and was also washed under running water, resulting in a calcium content of 2535 ppm and a sodium content of 23 ppm. Figure 12 is a graph of the viscosity for each of the colloidal solutions after washing. Figure 12 shows that the stability is greatly increased for both soles at 15% by weight and 18% by weight of diethylamine with demineralized water wash, as opposed to a wash with running water. Example 12
[0118] In order to investigate the photocatalytic activity of coatings prepared from soles in accordance with the concepts of the invention presently claimed and revealed, a thin layer of the colloidal suspension of the neutralized titania sol of Example 1 (with a weight ratio of 1: 1, from phosphoric acid to acetic acid), which was diluted with water to form a colloidal suspension of 10% titanium dioxide, was coated on a concrete wall (about 16L of 10% titanium dioxide sol by weight in an area of 135 m2) located in Camden London, England. (GPS coordinates of 51.5189 04 N and 0120685 W). NO and NO2, together with wind speed, wind direction, temperature and humidity were measured at 15-minute intervals. NO and NO2 were measured in a probe at a distance of 15 cm from the wall. Before coating the concrete wall with titanium dioxide sol, base measurements of NO and NO2 were taken in year 1 for the months of September to December. After the base measurements, the concrete wall was coated as described above and NO and NO2 were measured in year 2 for the months from September to December. The concrete wall was then covered with wood to cover the titanium dioxide sun coating, with NO and NO2 being measured in year 3 over the months from September to December. Figures 13 and 14 show the comparisons of the amounts of NO and NO2 in the baseline with the measured values, with the concrete wall coated with titanium dioxide sol and with the measurements with the concrete wall covered with wood. The comparisons show the average values of NO and NO2 measured at each hour of the day, for each day of the week during the months of September, October and December for years 1, 2 and 3, respectively. November data for each of these years was not used, because the levels of NO and NO2 were exceptionally low in other nearby locations, suggesting that there was another factor affecting the levels of NO and NO2 in that month. The comparisons also include only the NO and NO2 data, where the wind speed was less than 1.3 m / s. Figures 13 and 14 show that coating the concrete wall with titanium dioxide sol resulted in significant NOx removal activity over the reference levels. Figures 13 and 14 also show that, when covering the coating for the following year, the NOx levels basically returned to the reference levels, thus demonstrating the effectiveness of the titanium dioxide sol coating in reducing NOX.
[0119] Consequently, it has been demonstrated that titanium dioxide nanoparticle soles can be produced and that these colloidal solutions are useful to provide transparent photocatalytic coatings on a substrate, which are cleaners, self-cleaning, have stain resistance, being antibacterial, and / or antifungal / antimicrobial.
[0120] All references, including patent applications and publications cited herein, are hereby incorporated by reference in their entirety and for all purposes to the same extent as if each individual publication or patent, or patent application were specifically and individually indicated for incorporation by reference in its entirety for all purposes. Many modifications and variations of the concepts of the invention presently claimed and described can be made without departing from its spirit and scope, as will be apparent to those skilled in the art. The specific embodiments described herein are offered by way of example only, and the inventive concepts presently claimed and described should be limited only by the terms of the appended claims, together with the full scope of equivalents to which those claims are relevant.

权利要求:
Claims (9)
[0001]
1. Method to prepare a photocatalytic titanium dioxide sol, neutral, stable and transparent, CHARACTERIZED by the fact that it comprises the steps of: (i) reacting a hydrated titanium dioxide gel with an alkaline alkylating peptizing agent to provide a peptide alkaline titanium dioxide sol; and (ii) neutralize the peptide alkaline titanium dioxide sol with a combination of phosphoric acid and acetic acid to obtain a neutral, stable and transparent photocatalytic titanium dioxide sol comprising in the range of 0.5 to 20% by weight of titanium dioxide and comprising anatase crystallites.
[0002]
2. Method according to claim 1, CHARACTERIZED by the fact that the alkaline peptizing agent is present in the photocatalytic titanium dioxide sol, neutral, stable and transparent in an amount of 7% by weight to 20% by weight, based on the combined weight of the alkaline peptizing agent and titanium dioxide.
[0003]
3. Method according to claim 1, CHARACTERIZED by the fact that the alkaline peptizing agent is present in the photocatalytic titanium dioxide sol, neutral, stable and transparent in an amount of 18% by weight to 20% by weight, based on the combined weight of the alkaline peptizing agent and titanium dioxide.
[0004]
4. Method according to claim 1, CHARACTERIZED by the fact that the peptized alkaline titanium dioxide sol is neutralized with a combination of phosphoric acid and acetic acid; where the weight ratio of phosphoric acid to acetic acid is in the range of 0.8: 1 to 1.2: 1, and where phosphoric acid and acetic acid are simultaneously added to the peptized alkaline titanium dioxide sol .
[0005]
5. Method according to claim 1, CHARACTERIZED by the fact that the alkylamine is diethylamine.
[0006]
6. Method according to claim 1, CHARACTERIZED by the fact that the neutral, stable, transparent photocatalytic titanium dioxide sol comprises titanium dioxide crystallites having an average particle size less than 50 nm, at least 90 % of which are in anatase form.
[0007]
7. Method according to claim 1, CHARACTERIZED by the fact that the neutral, stable, transparent photocatalytic titanium dioxide sol is doped with a metal, in which the metal is selected from the group consisting of Ag, Zn, Mg, Sn, Fe, Co, Ni, Se, Ce, Cu and combinations thereof.
[0008]
8. Method according to claim 1, CHARACTERIZED by the fact that the neutral, stable, transparent photocatalytic titanium dioxide sol is washed with demineralized water so that the calcium ion concentration is less than 71 ppm and the sodium ion concentration is less than 13 ppm in the resulting neutral, stable, transparent photocatalytic titanium dioxide sol, and where the conductivity of the filtrate is equal to or less than 500 μS.
[0009]
9. Method according to claim 8, CHARACTERIZED by the fact that the neutral, stable, transparent photocatalytic titanium dioxide sun viscosity is less than 0.1 Pa.s (100 cP) after 4 weeks in room temperature.

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引用文献:

---

公开号 | 申请日 | 公开日 | 申请人 | 专利标题

---

---

GB8300554D0|1983-01-10|1983-02-09|Atomic Energy Authority Uk|Catalyst preparation|

---

DE3777931D1|1986-09-22|1992-05-07|Ishihara Sangyo Kaisha|TITANIUM DIOXYDSOL AND METHOD FOR THE PRODUCTION THEREOF.|

---

US5403513A|1987-10-07|1995-04-04|Catalyst & Chemical Industries, Co., Ltd.|Titanium oxide sol and process for preparation thereof|

---

JPS63215520A|1987-03-03|1988-09-08|Ishihara Sangyo Kaisha Ltd|Neutral titania and production thereof|

---

DE69530866T2|1994-10-05|2004-03-11|Toto Ltd., Kita-Kyushu|ANTIMICROBIAL SOLID MATERIAL, METHOD FOR THE PRODUCTION AND USE THEREOF|

---

EP1203617A1|1994-10-31|2002-05-08|Kanagawa Academy Of Science And Technology|Titanium dioxide photo catalyst structure|

---

US6387844B1|1994-10-31|2002-05-14|Akira Fujishima|Titanium dioxide photocatalyst|

---

US5897958A|1995-10-26|1999-04-27|Asahi Glass Company Ltd.|Modified titanium oxide sol, photocatalyst composition and photocatalyst composition-forming agent|

---

US6238738B1|1996-08-13|2001-05-29|Libbey-Owens-Ford Co.|Method for depositing titanium oxide coatings on flat glass|

---

WO1999058451A1|1998-05-14|1999-11-18|Showa Denko Kabushiki Kaisha|Titanium oxide sol, thin film, and processes for producing these|

---

US6569920B1|2000-08-16|2003-05-27|Millennium Inorganic Chemicals, Inc.|Titanium dioxide slurries having improved stability|

---

JP4521795B2|2000-11-08|2010-08-11|多木化学株式会社|Titanium oxide sol composition|

---

JP2002179949A|2000-12-11|2002-06-26|Hitachi Chem Co Ltd|Liquid for forming titania film, method of forming titania film, titania film and member made by using titania film|

---

US7060643B2|2000-12-28|2006-06-13|Showa Denko Kabushiki Kaisha|Photo-functional powder and applications thereof|

---

KR20030043536A|2001-11-28|2003-06-02|티오켐 주식회사|Synthesis of highly active photocatalytic TiO2-sol by hydrothermal method|

---

FR2838734B1|2002-04-17|2005-04-15|Saint Gobain|SELF-CLEANING COATING SUBSTRATE|

---

CN1218634C|2002-04-30|2005-09-14|香港中文大学|Method of preparing mesoporous titanium dioxide film with high disinfecting photoactivity|

---

US7521039B2|2002-11-08|2009-04-21|Millennium Inorganic Chemicals, Inc.|Photocatalytic rutile titanium dioxide|

---

KR100541750B1|2003-04-03|2006-01-10|선한엠엔티|Non-acidic, non-basic colloid solution containing dispersed titanium dioxide, method for preparing the same, and coating material comprising the colloid solution|

---

JP4540971B2|2003-12-05|2010-09-08|石原産業株式会社|Neutral titanium oxide sol and method for producing the same|

---

JP4522082B2|2003-12-05|2010-08-11|石原産業株式会社|Photocatalyst liquid composition and photocatalyst formed using the same|

---

WO2005083013A1|2004-01-30|2005-09-09|Millennium Chemicals|Coating composition having surface depolluting properties|

---

DE102005036427A1|2005-08-03|2007-02-08|Schott Ag|Substrate, comprising at least one fully or partially macrostructured layer, process for their preparation and their use|

---

US20070195259A1|2006-02-22|2007-08-23|Microban Products Company|Antimicrobial spectacle|

---

JP4606385B2|2006-06-05|2011-01-05|多木化学株式会社|Method for producing alkali-type titanium oxide sol|

---

JP4880410B2|2006-09-28|2012-02-22|多木化学株式会社|Member coated with photocatalytic coating composition|

---

ES2377227T3|2006-12-19|2012-03-23|Evonik Degussa Gmbh|Sol-gel process for the production of protective films for polymer substrates|

---

US7763565B2|2007-08-31|2010-07-27|Millennium Inorganic Chemicals, Inc.|Transparent, stable titanium dioxide sols|

---

US7820724B2|2008-02-14|2010-10-26|Millennium Inorganic Chemicals, Inc.|Colloidal titanium dioxide sols|

---

KR100935512B1|2008-05-15|2010-01-06|경북대학교 산학협력단|Manufacturing method of TiO2 photocatalyst and TiO2 photocatalyst manufactured by the same|

---

JP2010148999A|2008-12-24|2010-07-08|Taki Chem Co Ltd|Photocatalytic titanium oxide sol and method of manufacturing the same|

---

JP2011190152A|2010-03-16|2011-09-29|Tayca Corp|Amorphous titania sol and method for producing the same|

---

TWI604889B|2011-11-16|2017-11-11|克里斯朵美國公司|Neutral, stable and transparent photocatalytic titanium dioxide sols|US9528009B2|2011-04-15|2016-12-27|Craig Grossman|Composition and method to form a self decontaminating surface|

---

KR102008122B1|2011-04-15|2019-08-06|얼라이드 바이오사이언스, 인크.|Composition and method to form a self decontaminating surface|

---

US11166458B2|2011-04-15|2021-11-09|Allied Bioscience, Inc.|Wet wipes comprising antimicrobial coating compositions|

---

TWI604889B|2011-11-16|2017-11-11|克里斯朵美國公司|Neutral, stable and transparent photocatalytic titanium dioxide sols|

---

WO2013138298A1|2012-03-16|2013-09-19|Intecrete, Llc|Multi-layered cement compositions containing photocatalyst particles and method for creating multi-layered cement compositions containing photocatalyst particles|

---

WO2014118372A1|2013-02-02|2014-08-07|Joma International A/S|An aqueous dispersion comprising tio2 particles|

---

EP2950924A1|2013-02-03|2015-12-09|Joma International AS|A catalytic substrate surface containing particles|

---

GB2521405B|2013-12-18|2015-12-02|Dublin Inst Of Technology|A surface coating|

---

CN104626680B|2015-03-03|2016-09-07|中国科学院上海硅酸盐研究所|A kind of composite black titanium deoxid film and preparation method thereof|

---

ES2807874T3|2015-10-21|2021-02-24|Tronox Llc|Nox reducing coatings and methods to reduce Nox with them|

---

CN108463435A|2015-11-20|2018-08-28|克里斯特尔美国有限公司|Titanium dioxide composition is with it as the purposes for preventing pollutant|

---

EP3377446B1|2015-12-10|2019-04-03|Cristal USA Inc.|Concentrated photoactive, neutral titanium dioxide sol|

---

WO2017156372A1|2016-03-10|2017-09-14|Cristal Usa Inc.|Photocatalytic coating compositions|

---

KR101856971B1|2016-12-20|2018-05-15| 클레어|Method for preparing Sickhouse Syndrome Remover by combining with Photocatalyst and Fermented Acid|

---

CN107352579A|2017-07-17|2017-11-17|上海友兰科技有限公司|A kind of preparation method of superhydrophilic self-cleaning TiO 2 sol|

---

CN107917351A|2017-10-27|2018-04-17|中山市汉庭照明科技有限公司|A kind of LED light bulbs and preparation method having except effect of formaldehyde|

---

IT201800003836A1|2018-03-21|2019-09-21|Andrea Gaglianone|COMPOSITION AND SANITATION METHOD FOR THE SANITIZATION-PURIFICATION OF SURFACES AND ENVIRONMENTS|

---

US20210015952A1|2018-06-19|2021-01-21|Northwestern University|Silver and titanium dioxide based optically transparent antimicrobial coatings and related methods|

---

CN108967442B|2018-07-24|2020-06-05|广东省生态环境技术研究所|Ferrous modified selenium sol for inhibiting cadmium and arsenic accumulation of rice and preparation method and application thereof|

---

TW202021465A|2018-12-10|2020-06-16|愛爾蘭商卡斯特斯科技公司|P-doped surface coatings and process of preparation thereof|

---

US20220025194A1|2018-12-10|2022-01-27|Kastus Technologies Dac|P-doped surface coatings and process of preparation thereof|

---

PL428604A1|2019-01-16|2020-07-27|Bolix Spółka Akcyjna|Method of protecting a newly constructed facade against microbiological contamination and method of renovation of a building facade affected by microbiological contamination|

---

CN110090571A|2019-04-01|2019-08-06|江苏奥净嘉环保科技有限公司|A kind of preparation method of nano titanium oxide dispersion|

---

DE102020110567A1|2020-04-17|2021-10-21|Mursall Aktive Coating GmbH|Process for applying a coating to a glass surface|

---

US11253842B1|2021-04-02|2022-02-22|TiCoat, Inc.|Titanium dioxide containing peroxo titanium complex and methods of manufacturing and application of the same|

法律状态:
2019-07-16| B06F| Objections, documents and/or translations needed after an examination request according [chapter 6.6 patent gazette]|

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2019-07-30| B06U| Preliminary requirement: requests with searches performed by other patent offices: procedure suspended [chapter 6.21 patent gazette]|

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2019-10-01| B25A| Requested transfer of rights approved|Owner name: TRONOX LLC (US) |

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2020-03-31| B07A| Application suspended after technical examination (opinion) [chapter 7.1 patent gazette]|

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2020-10-27| B09A| Decision: intention to grant [chapter 9.1 patent gazette]|

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2020-12-15| B16A| Patent or certificate of addition of invention granted [chapter 16.1 patent gazette]|Free format text: PRAZO DE VALIDADE: 20 (VINTE) ANOS CONTADOS A PARTIR DE 16/11/2012, OBSERVADAS AS CONDICOES LEGAIS. |

优先权:

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申请号 | 申请日 | 专利标题

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US201161560669P| true| 2011-11-16|2011-11-16|

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US61/560.699|2011-11-16|

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PCT/US2012/065616|WO2013074984A1|2011-11-16|2012-11-16|Neutral, stable and transparent photocatalytic titanium dioxide sols|

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