Patent Application
20100075836
This invention relates generally to use of ultraviolet photocatalytic oxidation (UV-PCO) technology for the improved decontamination of fluids in fluid purifier systems. More specifically, the present invention relates to a method of making photocatalytically active oxides used in UV-PCO technology for the decontamination of air in air purifier systems.
Some buildings utilize air purification systems to remove airborne substances such as benzene, formaldehyde, and other contaminants from the air supply. Some of these purification systems include photocatalytic reactors that utilize a substrate or cartridge containing a photocatalyst oxide. When placed under an appropriate light source, typically a UV light source, the photocatalyst oxide interacts with airborne water molecules to form hydroxyl radicals or other active species. The hydroxyl radicals then attack the contaminants and initiate an oxidation reaction that converts the contaminants into less harmful compounds, such as water and carbon dioxide. It is further believed that the combination of water vapor, suitably energetic photons and a photocatalyst also generates an active oxygen agent like hydrogen peroxide as suggested by W. Kubo and T. Tatsuma Analytical Sciences 20 (2004) 591-593.
A commonly used UV photocatalyst is titanium dioxide (TiO2), otherwise referred to as titania. Degussa P25 titania and tungsten dioxide grafted titania catalysts (such as tungsten oxide on P25) have been found to be especially effective at removing organic contaminants under UV light sources. See, Patent Publication US2004/00241040 “Tungsten oxide/titanium dioxide photocatalyst for improving indoor air quality” by Wei et al.
A problem with air purification systems using UV-PCO technology has arisen. Currently available systems exhibit a significant loss in catalytic ability over time. This loss of catalytic ability has been attributed, at least partially, to volatile silicon-containing compounds (VSCC), such as certain siloxanes, in the air.
The aggregate amount of volatile organic compounds (VOC) in air is typically on the order of 1 part per million by volume. In contrast, VSCC concentrations are typically two or more orders of magnitude lower. These VSCC arise primarily from the use of certain personal care products, such as deodorants, shampoos and the like, or dry cleaning fluids, although they can also arise from the use of RTV silicone caulks, adhesives, lubricants and the like. When these silicon-containing compounds are oxidized on the photocatalyst of a UV-PCO system, they form non-volatile compounds containing silicon and oxygen that deactivate the photocatalyst. Examples of non-volatile compounds of silicon and oxygen include silicon dioxide, silicon oxide hydroxide, high order polysiloxanes and the like. Increasing the catalyst surface area alone does not necessarily slow the rate of deactivation as might be expected if the deactivation were caused by direct physical blockage of the active sites by the resultant non-volatile compound containing silicon and oxygen.
There is a need for improved UV-PCO systems that can aid in the elimination of fluid borne contaminants in a fluid purifier and can operate effectively in the presence of typically encountered levels of volatile silicon-containing compounds such as siloxanes.
An improved UV photocatalyst made up of porous particles formed by wide band gap semiconductor crystallites is formed using a sol-gel process to create a porous structure. The particles preferably have a porous structure with pores of a diameter of about 4 nm or greater and surface area of greater than about 190 m2/cm3 of skeletal volume. The process includes photocatalyst template creation, template conditioning, template refinement, and coating application.
The template creation utilizes a hydrolysis reaction using an organometallic precursor within an aqueous solution that includes a polymer, surfactant, oligomer, or chelating agent. The solution may also include an organic or inorganic acid, and a metal salt that when combined with oxygen forms a metal oxide semiconductor. Following the hydrolysis reaction, the sol may be aged to achieve the desired surface area and pore size.
Template conditioning of the catalyst material produced by the hydrolysis reaction results in the isolation, purification and “locking in” of the solid material with a specific template. Template conditioning may include filtering and refluxing with a solvent having a lower surface tension than water.
Template refinement transforms the template structure into a material having a specific phase composition, crystallinity, surface area and pore size distribution. Template refinement may include an optional low temperature drying step followed by a high temperature calcination step.
Coating application is performed by mixing the powder obtained from calcination with a solvent to form a slurry. The slurry is then applied to a substrate.
Deactivation resistant photocatalysts can be formulated by layering one or more photocatalysts on a suitable substrate such as, but not limited to, an aluminum honeycomb. These deactivation resistant photocatalysts may also be used in so-called backside illumination designs where the photocatalyst is deposited on light pipes, light carrying fibers or structures, where the photons enter from the photocatalytic layer opposite that which is exposed to the fluid flow.
In the illustration shown in
The porous structure of particle 16 provides a large surface area, large cylindrical pore photocatalyst. Pores 20 are believed to provide available void space for deposition or location of non-volatile compounds of silicon and oxygen resulting from conversion of the volatile silicon-containing species, so that the non-volatile products do not block active sites on the photocatalyst. As a result, the deactivation of the photocatalyst is reduced.
One preferred photocatalyst is titanium dioxide, including suitably doped titanium dioxide where the dopant increases the photocatalytic activity, and metal oxide grafted titanium dioxide catalysts, such as, but not limited to tungsten oxide grafted TiO2 The present invention also contemplates the use of photocatalytic mixed metal oxides; an intimate such as but not limited to tin oxide (SnO2), indium oxide (In2O3), zinc oxide (ZnO), iron oxides (FeO and Fe2O3), neodymium oxide (Nd2O3) and cerium oxide (CeO2).
If siloxanes or volatile silicon-containing compounds are expected to be encountered, then the photocatalyst or photocatalytic layer should have increased surface area relative to P25 titania, and this surface area should primarily be in a pore structure with low mass transfer resistance such as in pores with a diameter of about 4 nm or greater as measured by the BJH adsorption technique. The pore diameter may be measured by the BJH technique that is well known to those skilled in the art and is typically an option on automated surface area determination equipment. The original reference describing the BJH technique is E. P. Barrett, L. G. Joyner, P. P. Halenda, J. Am. Chem. Soc. 73, (1951), 373-380.
Higher surface area in pores substantially less than 4 nm in diameter does not increase the resistance to deactivation by siloxanes. For adequate photocatalytic activity, the crystallites of the wide band gap semiconductor (or semiconductors) that make up this porous structure must possess sufficient size (typically greater than about 2 nm in diameter) and the appropriate degree of crystallite perfection to allow adequate electron-hole separation to occur. According to Degussa Technical Information TI 1243, March 2002, P25 titania has a BET surface area of 50 m2/g and consists of aggregated primary particles with an average size of 21 nm. Of these primary particles, 80% are anatase, and 20% are rutile. The anatase particles tend to be somewhat smaller and the rutile somewhat larger. In practice P25 titania based photocatalytic material has a measured BET specific surface area of between about 44 m2/g and about 55 m2/g. BET surface area is described in S. Brunauer, P. H. Emmett, and E. Teller, J. Am. Chem. Soc. 60, (1938), 309-319.
Since specific surface area is measured in m2/gram, the surface area has to be corrected for the potentially different densities of different photocatalysts. For example, the anatase form of TiO2 has a density of 3.84 m2/g, while rutile form has a density of 4.26 m2/g. In contrast, tin oxide (SnO2) as cassiterite has a density of 6.95 m2/g, while zinc oxide (zincite) has a density of 5.61 m2/g. Thus, to convert to m2/cm3 of skeletal volume, an 80% anatase 20% rutile mix has a surface area per cm3 of skeletal volume of [(0.8×3.84 g/cm3)+(0.2×4.26 g/cm3)]*50 m2/g=196.2 m2/cm3.
Template creation 32 of the nanoengineered photocatalyst is dependent upon several factors, which include the choice of an organometallic precursor, composition of solvent medium, control of the hydrolysis of an organometallic precursor, control of condensation reactions that occur concurrently or after hydrolysis of the organometallic precursor, and the time needed to age a sol to create a template for a material that has a surface area greater than about 190 m2/cm3 of skeletal volume (and preferably greater than about 250 m2/cm3 of skeletal volume) with well defined pores.
Substituents on the titanium organometallic precursor are expected to contribute to the hydrolysis reaction in the following manner in an aqueous solvent with no additives: halogens will hydrolyze faster than isoproxide which will hydrolyze faster than t-butoxide.
Coordination of organometallic precursor can affect the amount of oligomerization than could occur after hydrolysis and ultimately will affect the gel structure.
The concentration of the precursor should decrease the rate of hydrolysis when the precursor is diluted with a solvent that does not interact with the precursor. Interaction with the dilution solvent would mean that hydrolysis has started prematurely before contact with the intended solution.
Purity of the titanium organometallic precursor has not been observed to be critical in the synthesis of about 100 to about 130 m2/g titanium oxide with a controlled pore distribution. Titanium isopropoxide of 97% to 99.999% purity has been used with no differences in the overall reaction product.
The rate of addition of the titanium organometallic precursor can also control the hydrolysis reaction in such a manner that the faster the addition, the faster the hydrolysis in an aqueous solution. Using titanium isopropoxide and conditions described for the standard example, a rate of 4 drops/5 sec has been found to produce a titanium oxide material with a surface area >100 m2/g and the incremental surface area was greater than 15 m2/g. Increasing the rate of addition produces a lower surface area titanium oxide.
The rate of hydrolysis is also affected by the medium in which the hydrolysis reaction occurs. When aqueous or protic or polar solvents are used as the bulk medium, hydrolysis would be expected to occur, whereas non-aqueous or aprotic or non-polar solvents would not participate in hydrolysis. A combination of small aliquot of aqueous, protic or polar solvent rapidly mixed with a large volume of nonaqueous, aprotic or non-polar solvent would result in a medium where a controlled hydrolysis could occur due to the dilution of the reactive medium.
The pH of a medium will also affect the rate of hydrolysis of the titanium organometallic precursor such that in acidic environments, the hydrolysis reaction will occur at a faster rate. The pH of the medium can be critical to the concentration, shape, and size of the dynamic entanglements that result from the polymer interactions with the medium.
The choice of polymer present in the bulk medium may affect the hydrolysis rate if the polymer changes the pH or viscosity of the bulk medium. The choice of polymer and solvent will result in the formation of dynamic entanglements of the polymer that will influence the size and shape of the hydrolysis and condensation products. In general, polymers interact with solvent by either an attraction to the solvent, repulsion of a solvent, or the polymer chain reaches an equilibrium state with the solvent. When the polymer is attracted to solvent, the polymer chains are extended away from other polymer chains and large void spaces within the polymer chains result. In a solvent that lacks attraction to a polymer chain, the polymer chains are more attracted to other polymer chains, and the void spaces are smaller than those void spaces that would exist if polymer chains were more attracted to a solvent. Another means of phrasing the previous example is that the polymer chains collapse on and amongst other polymer chains. Under equilibrium conditions, or theta solvent conditions, the void spaces of the polymer chains result from the balance of attractive and repulsive forces existing in the polymer solvent solution. All of the above described scenarios are affected by temperature.
The addition of metal salts to an aqueous solution would be expected to provide additional interaction with the polymer solvent interactions, and thus contribute to changes in the resulting void space which ultimately affects phase, shape, surface area, particle size and pore size distribution of the end material. In an aqueous solution, the dissociation of the metal salt results in the separation of the cation and anion species. Depending on the nature of the ionic species and the reactivity of the anion and cation, further reaction with the solvent e.g., acid can result in the formation of a new chemical present in solution that can interact with the existing polymer. For example, when tin fluoride is added to an aqueous 1M acetic acid solution containing polyethylene glycol (PEG), the dissociation of the salt results in the formation of tin and fluoride ions. When the initial drop of an organic metallic precursor is added, the hydrolysis reaction that occurs also initiates an addition reaction where the tin ions combine with acetate ions to form tin(II) acetate. Acetate ions are much larger than tin or fluoride ions, the size of tin(II) acetate would be the equivalent of the diameter of one tin atom plus two acetate molecules. The tin(II) acetate is a large bulky spacer group that can interact and hence orient the PEG in solution.
The type of salt can also influence the final material. If the salt contains the cation of a known semiconductor oxide, then incorporation of the salt into metal vacancies of the main metal oxide material may result in a material with a band gap that is altered from both the parent metal oxide (material being produced) and cation-based metal oxide. A similar scenario would exist for non-oxide based metal salts as long as the necessary anion was incorporated into the parent material.
After the hydrolysis reaction is complete, the aging of the sol is critical for formation of the polymer network and the crystallization of the titanium oxide particles formed. Differences in surface area and pore size distribution result when aging time varies from 0 hours to 3 weeks. Aging times under 72 hours result in materials with lower surface areas (<100 m2/g) and incremental pore areas under 15 m2/g. Aging times over 168 hours do not produce dramatic improvements in surface area or incremental pore area compared to aging for 72 hours. Higher surface areas and incremental pore areas are obtained when the sol is gently stirred over the duration of aging. In the absence of stirring during the aging process, a material with lower surface area and incremental pore area is obtained i.e., less than 100 m2/g and incremental pore area under 15 m2/g.
The pore diameter may be measured by the BJH technique that is well known to those skilled in the art and is typically an option on automated surface area determination equipment.
Template conditioning 34 results in the isolation, purification and a “locking in” of the solid material with a specific template after the template creation step. After isolation of the solid from the liquid sol, residual water and potentially other impurities from the sol are removed and the solid is isolated under reduced pressure.
Isolation of the solid produced in the sol during template formation, may be accomplished by vacuum filtration, gravity filtration, centrifugation. The resulting solid may also be isolated under reduced pressure e.g., rotoevaporation, however the affect of pressure will alter the template of the solid such that in the case of titanium oxide, materials with lower surface areas (<100 m2/g) and incremental pore areas under 15 m2/g will result. Depending on the composition of the sol, the isolated solid may need to be washed with small aliquots of solvent several times to remove potential contaminants or undesirable materials that could ultimately prevent the formation of a desired phase, structure, crystallinity, etc.
Reflux of the isolated solid with a solvent that has a lower surface tension than water results in the removal of water and water-based impurities trapped internally within the solid providing that the solvent is protic or aprotic. For solvents that have a higher surface tension than water, it is believed that solvent would become trapped within vacant pores and limit the surface area and pore size distribution of the resulting material.
Time of reflux is proportional to the amount of water removed. For example a one hour reflux time will remove more water than a reflux time of 15 minutes. After reflux times of one hour or greater, the solid particles form an emulsion within the solvent water mixture and solid particles do not appear to settle up to 24 hours post reflux.
The volume of solvent used for reflux should always be in excess of the amount of water or water-based impurities that are predicted to be removed. For 10 g of solid material, 300 ml of solvent would be appropriate to perform a successful reflux. A repeat reflux step can ultimately result in additional removal of water and/or water based impurities. In order to repeat reflux, the solid must be isolated by filtration or centrifugation means. Solvent removal at reduced pressure prior to reflux would negatively alter the template and result in material with lower surface areas (<100 m2/g) and incremental pore areas under 15 m2/g in the case of titanium oxide materials.
The solid in the emulsion created in the reflux step must be isolated under reduced pressure to “lock-in” a structure template. In the case of titanium oxide, by removing solvent so that the solvent is distilled off at 40° C., a suitable template is produced that after refinement can result in a material having a surface area greater than 100 m2/g and an incremental pore area of 15 m2/g or greater.
It is believed that under reduced pressure, the organic and polymer components “lock” the placement of the titanium oxide network. The application of higher distillation temperatures and pressures result in a collapse of the network for titanium dioxide, while the use of lower temperatures and pressures may not effectively remove solvent from the solid material. Failure to remove solvent will result in a decrease of surface area and incremental pore area.
Template refinement 36 of the template structure may include an optional low temperature drying step followed by a high temperature calcination step. For some preparations a low temperature drying step is critical for removal of residual solvent vapors. A high temperature calcination step will transform the template structure into a material with a specific phase composition, crystallinity, particle size, surface area, and pore size distribution.
Depending on the polymer type, polymer concentration and reflux solvent, a low temperature (i.e., 100° C. or less), reduced pressure drying step may be necessary to remove residual contaminants. For examples where titanium oxide was produced, preparations that used polymer amounts greater than 4 g or preparations that did not use a metal salt had higher surface areas when a 12 hours vacuum drying step was employed prior to calcination. When 4 g of polymer, and 1.5 g of metal salt were used, a vacuum drying step resulted in lower surface area after calcination.
Calcination is done either following the isolation of the material by rotoevaporation or after a low temperature drying step is implemented. Calcination temperature is critical to produce a desired phase. For titanium oxide, temperatures above 700° C. typically produce a photochemically inactive rutile phase. Temperatures between 300° C. to 600° C. will produce an anatase phase which is regarded to be photochemically active.
Coupled with temperature are the rate of heating, duration of heating, and atmosphere of calcination. All of the mentioned variables are critical for control of phase, crystallinity, surface area, and pore size.
The following calcination examples apply to a titanium oxide material prepared by the hydrolysis of titanium isopropoxide in an aqueous acidic PEG 4600, tin fluoride medium and worked up by isolation of the solid, 1 hour reflux, removal of solvent by at 40° C. under reduced pressure.
For calcination experiments of 4 hours (at temperature) with a constant air purge at a heating rate of 3° C./min:
At 400° C., the resulting surface area was less than 100 m2/g and the incremental surface area was less than 15 m2/g. The presence of organic material was evident by the brown discoloration on the powder (powder should be white) and verified by thermogravimetric analysis.
At 500° C. and 550° C., the resulting surface area was greater than 100 m2/g and the incremental surface area was greater than 15 m2/g. Two to three pore size distributions exist from 0 nm to 50 nm. Materials produced are greater than 95% anatase with 5% rutile. Crystallite size has been measured using powder X-ray diffraction at approximately 13 nm.
At 700° C., the resulting surface area is under 50 m2/g, incremental pore area is less than 5 m2/g. Compared to the above calcination experiments where there are two distinct pore size distributions, at 700° C., five pore size distributions exist over a range of 0 nm to 100 nm. The major phase for this material is expected to be anatase. Crystallite size is predicted to be greater than 13 nm.
The atmosphere in which the calcination occurs can influence the phase, crystallinity, surface area, and pore size. Ideally for the decomposition of organic matter, it is conducive to have an oxygen rich environment. At 500° C., there is no substantial difference in surface area or incremental pore area when using air compared to using a 50/50 mixture of O2/N2. Despite the lack of change in surface area, one may expect changes in crystal size and phase.
Coating application 38 uses the powder obtained after calcination. The powder is mixed with a solvent to prepare a slurry. This slurry is applied to a substrate, and can be further dried.
The critical steps in the preparation of the slurry pertain to the reduction of agglomerates within the solution and the extent of incorporation of the solid powder into a solvent. Agglomerates in the powder may be reduced by sonication in a desired solvent or centrifugal mixing with appropriate milling media. Critical to all agglomeration methods is the ability to not introduce additional contamination.
Incorporation of the solid into the solvent may be accomplished by the use of but not limited to mechanical stirring, centrifugal mixing, magnetic stirring, high shear mixing.
The slurry can be applied to a substrate by spray coating, dip coating, electrostatic coating or thermal treatment to a substrate. The coated substrate can be dried at room temperature, dried on hot contact, or vacuum dried at either room or elevated temperature.
The polymer component may be, for example, polyethylene glycol with a number average molecular weight (Mn) such as 200, 500, 2000, 4600, or 10,000. The polymer component may also include surfactants and chelating agents, such as citric acid, urea, poloxyethyleneglycol (e.g. Brij®) surfactants, an ethylene oxide/propylene oxide block copolymer (e.g. Pluronic 123®), polyvinyl alcohol, polyvinyl acetate, D-sorbitol and other hydroxyl-containing compounds. Other polymers, oligomers, surfactants, or chelating agents that contain chemical functionalities that can interact with the reaction contituents may be used as it is believed that the polymer, oligomer, surfactant or chelating agent contributes to the initial gel structure which contributes to (directs or creates a template for) the resulting particle morphology and structure during calcination.
Solvents may include, but are not limited to water, alcohols or organic-based solvents or mixtures thereof. The preferred solvent is water with controlled concentrations of added acid, base or salt. For example, the acid may be an organic acid such as acetic acid (e.g. 1M, 4M, 0.5M, 0.25M) or an inorganic acid such as hydrochloric acid (1M). The base may be sodium hydroxide (1M). The salt may be sodium chloride (1M).
The solution may also include one or more additional metal salts, wherein the metal is one that, when combined with oxygen, forms a wide band gap metal oxide semiconductor. Examples of metal salts include tin(IV) fluoride, iron(II) acetylacetonate, iron(III) acetylacetonate, neodymium(III) acetylacetonate, zinc(II) acetate hydrate, and cerium(IV) fluoride. The choice and concentration of metal salt will affect the pore shape of the resulting catalyst material. It is believed that the addition of a metal salt contributes to the formation of a discrete porous network, and may also contribute to increased photocatalytic activity compared to commercial titanium oxide materials.
Other salts, acids and bases (and combinations thereof) may be used as long as the interaction between the salt, solvent and polymer results in less than 5 populations of discrete pore size distributions in the isolated photocatalyst, which is material isolated following removal of the salt, solvent and polymer. The combination of polymer, salt, and solvent is important as the interactions between the solvent and the polymer are believed to control initial formation and structure of the gel network.
Depending on the choice of solvent, polymer chains in solution will adopt dynamic random conformations that will result in regions varying in polymer concentration. These regions may be defined by globules or coils. Globules are regions of high polymer concentration where polymer chains are dense, compact and possess minimal void spaces. Coils are more relaxed regions of polymer chains where void spaces are present. It is believed that the hydrolysis reaction of the metal precursor occurs within the confines of the polymer void spaces. A metal salt, such as tin fluoride, in the solution, can dissociate into ions and further interact with other components in solution or titanium dioxide produced by the hydrolysis of the initial titanium precursor. The resulting chemical species formed from the dissociation of the metal salt can either act as spacers or as crystal surface control agents. In addition, the resulting tin oxide semiconductor, in conjunction with the titanium dioxide semiconductor, may yield enhanced photocatalytic activity. When tin fluoride is introduced into an aqueous acetic acid solution, it dissociates, and tin acetate is formed. The addition of titanium-based precursors into this aqueous solution starts a chemical reaction and forms oxidized titanium products, such as titanium dioxide.
A typical example of the above described catalyst would be when 20 ml of titanium isopropoxide, 99%, is hydrolyzed in a solution containing 100 ml of aqueous 1M Acetic acid, 4.00 g of 4400-4800 Mn polyethylene glycol, and 1.5 g of tin(II) fluoride, 99%. The combination of the polymer, the acetic acid, and the tin acetate form a dynamic entanglement, and the voids within the entanglement are most likely where the crystallites of titanium dioxide form. As a result, the titanium dioxide is surrounded by regions of polyethylene glycol, acetate, metal acetate, and hydroxyl groups from water and from polyethylene glycol.
When the hydrolysis reaction is complete, the sol is aged (step 42). Aging times range from about 0 hours to about 3 weeks, and preferably are in a range of about 72 hours to about 168 hours. The sol may be stirred during the aging process.
Template conditioning 34 isolates, purifies and locks in the catalyst material with a specific template. It includes filtration (step 44), reflux (step 46) and rotoevaporation (step 48).
The hydrolysis reaction (step 40) and subsequent aging (step 42) produces a dispersion or mixture of powder and solution. The mixture is filtered (step 44), and is then refluxed in the presences of alcohol or aprotic solvent to remove some of the water that remains in the material, most likely inside the pores (step 46). Water has a high surface energy, and is expected to cause some of the pores to collapse as the solid structure is dried. Alcohol, on the other hand, typically has a lower surface tension, and is expected to readily evaporate without collapsing the pore structure of particle 16.
Reflux of the mixture (step 46) is then followed by solvent removal, preferably using reduced pressure methods, such as a rotoevaporation process (step 48). It is desirable to control the pressure used to remove the solvent, such that the solvent vapor distillation will occur at a controlled temperature. In one example, the pressure during solvent removal was controlled so that solvent vapor was distilled at 40° C.
Template refinement 36 includes optional drying (step 50) and calcination (step 52). The product may be dried, preferably at pressures below one atmosphere, to remove most of the non catalytic material (step 50). Drying takes place under reduced pressures at a temperature typically between about 25° C. and about 100° C. In one embodiment, drying is performed for about 2 days at about 75° C., under conditions in which low vapor pressure impurities are removed. Various desirable combinations of time, temperature and pressure can be used to carefully control the drying and to remove to non-catalytic materials to a content below about 10% by weight.
Calcination is performed at temperatures in a range of about 350° C. to about 700° C. (step 52). In one embodiment, the product is heated from room temperature to about 500° C. at a rate of about 3° C. per minute. The temperature is then held at about 500° C. for about four to about 18 hours, and then is reduced back to room temperature. The calcination step removes any residual non-catalytic materials, so that the resulting porous particles are about 100 nm in diameter and are made up of crystallites of wide band gap oxide semiconductor in a pore structure having pores of diameter 4 nm or larger.
During calcination, oxygen enrichment may be used to assist in the removal of organic materials. The oxygen enrichment, however, is controlled so that it does not trigger an exothermic oxidation and cause a transition from the anatase phase of TiO2 to the rutile phase.
As a result of calcination, the product is in the form of a white powder, with porous particles forming clusters of about 1 micron to about 2 micron diameter.
Coating application 38 includes aqueous slurry formation (step 54) and application to a substrate (step 56). The powder is mixed with water or organic solvent to form a slurry having approximately 1-20 wt % solids (step 54). The slurry is then applied to substrate by spraying, dip coating, or other application technique (step 56). Solvent evaporates, leaving the catalyst film having a thickness on the order of about 3 microns to about 6 microns thickness. Approximately 1 milligram catalyst per square centimeter is desirable. Greater than about 1 milligram per square centimeter does not significantly increase the photocatalytic properties of the film. An amount significantly less 1 milligram per square centimeter will result in a lower photocatalytic effect.
The data point for conventional P25 titanium dioxide photocatalyst shows a deactivation rate of slightly greater than 2 and a cumulative surface area of less than 20 m2/g in pores of greater than 4 nm in diameter. In contrast, all of the other photocatalyst exhibited a deactivation rate of 1.5 or lower and the surface area of 40 m2/g or greater in pores of greater than 4 nm diameter. These represent improvements of X-Y % reduction in deactivation rates relative to P25.
UV139 is a photocatalyst according to the process shown in
In separate experiments, photocatalyst 2UV45, 2UV59, and UV114 were formed using the method with polyethylene glycol, acetic acid, titanium isopropoxide, and with tin fluoride as the metal salt in the aqueous solution. For each of samples 2UV45, 2UV59, and UV114, during solvent removal using rotoevaporation, a reduced pressure was used.
In separate experiments for preparing samples 2UV91, 2UV106, and 2UV117, the vacuum during rotoevaporation was controlled to 137 millibar. Sample 2UV91 was a batch using four grams of polyethylene glycol (Mn=4600); 1.5 grams tin fluoride; 100 milliliters acetic acid (1M); and 20 milliliters titanium isopropoxide (97% solution). Samples 2UV106 and 2UV117 used the same components in twice the quantity.
All of the synthesized photocatalysts had increased photocatalytic efficiency compared to Degussa P25 titania as a result of surface area greater than 50 m2/g (or greater than about 190 m2/cm3 of skeletal volume), a discrete number of high population pore diameters, e.g., one, two or three different pore diameter populations as opposed to Degussa P25 that has greater than five populations of pore diameters. In addition to improved photocatalytic activity, the synthesized photocatalysts also exhibited improved resistance to siloxane contamination compared to the commercial P25 titanium oxide photocatalyst.
1 ppm propanol was oxidized by UV-A light at 50% relative humidity under conditions where initially about 20% of the propanol was oxidized. The deactivation agent was 90 ppb hexamethyldisiloxane. Under these conditions increasing the surface area of pores greater than 4 nm from 18.5 m2/g (˜72.6 m2/cm3 by BJH N2 adsorption in P25 titania) to 77.8 m2/g, (i.e., ˜298.8 m2/cm3) in tin doped anatase TiO2 (designated UV114) decreased the rate of deactivation from 2.05% initial activity/hr for P25 to 0.335% initial activity/hr for UV114. Thus the P25 titania would drop to 50% of its initial activity in about 24 hours at 90 ppb, or 90 days at 1 ppb. In contrast, the UV 114 activity would reach 50% of its initial activity in 550 days of continuous operation when challenged with 1 ppb hexamethyldisiloxane if the deactivation rate is proportional to the siloxane concentration.
It is preferred that the photocatalyst has a skeletal or crystallite density of 3.84 g/cm3 and a surface area of greater than 50 m2/gram (or greater than about 190 m2/cm3 of skeletal volume) in pores 4 nm or greater diameter as measured with nitrogen by adsorption. It is especially preferred that the surface area in pores greater than or equal to 4 nm diameter be greater than 50 m2/gram where the surface area and pore diameter is measured with nitrogen by adsorption and the data analyzed by the BJH method. As other photocatalytic oxides with different densities may be used, this can be expressed as greater than about 190 m2/cm3 of photocatalytic skeletal volume. In these examples, the conventional BET specific surface area measurement of m2/g is used for convenience.
Further experimental details are described herein for typical measurements of photocatalyst deactivation. Substrates were coated with an aqueous suspension of P25 Degussa titania and allowed to dry. The P25 coating was positioned to absorb 100% of the incident light when used in a flat plate photocatalytic reactor with UV illumination provided by two black-light lamps (SpectroLine XX-15A). The spectral distribution was symmetric about a peak intensity located at 352 nm and extended from 300 nm to 400 nm. The intensity was selected by adjusting the distance between the lamp and the titania-coated substrate. UV intensity at the reactor surface was measured by a UVA power meter (Oriel UVA Goldilux). High-purity nitrogen gas was passed through a water bubbler to set the desired humidity level. The contaminants were generated either from a compressed gas cylinder such as Propanal/N2, or a temperature controlled bubbler. An oxygen gas flow was then combined with the nitrogen and contaminant flows to produce the desired carrier gas mixture (15% oxygen, 85% nitrogen).
The titania-coated aluminum or gas slides were placed in a well milled from an aluminum block, and covered by a quartz window (96 percent UVA transparent). Gaskets between the quartz window and aluminum block created a flow passage of 25.4 mm (width) by 2 mm (height) above the titania-coated slides.
Contaminated gas entered the reactor by first passing through a bed of glass mixing beads. Next, the gas flow entered a 25.4 mm by 2 mm entrance region of sufficient length (76.2 mm) to produce a fully-developed laminar velocity profile. The gas flow then passed over the surface of the titania-coated glass-slides. Finally, the gas passed through a 25.4 mm by 2 mm exit region (76.2 mm long) and a second bed of glass beads before exiting the reactor.
The longevity of various TiO2 based photocatalysts in the presence of 90 ppb hexamethyldisiloxane was determined using the above reactor. The deactivation rate was determined by the slope of a straight line best representing the catalyst performance during its initial stages of operation. The P25 value represents the average results from multiple tests. The rate of activity loss expressed in % initial activity per hour becomes smaller, that is tends towards zero as the surface area in pores greater than or equal to 6 nm becomes larger. This is not the case with the BET surface area, or the surface area in pores greater than 4 nm in diameter as determined by N2 adsorption and BJH analysis of this adsorption as performed by a Micromeritics ASAP 2010 surface area determination unit.
The typical example provided is for the production of high surface area (100-130 m2/g) cylindrical pore titanium oxide. The following example is a typical variation for changing the pore shape of the catalyst material. Using the typical formulation described above, the substitution of 1.5 g of neodymium acetyl acetonate for 1.5 g of tin (II) fluoride, results in a catalyst material of ˜80 m2/g with an “ink bottle” pore shape.
In a similar fashion, the substitution of the 0.298 g of zinc(II) acetate hydrate results in a material having a surface area of ˜125 m2/g and an intermediate pore shape between a cylindrical and “ink bottle” shape.
While the invention has been described with reference to an exemplary embodiment(s), it will be understood by those skilled in the art that various changes may be made and equivalents may be substituted for elements thereof without departing from the scope of the invention. In addition, many modifications may be made to adapt a particular situation or material to the teachings of the invention without departing from the essential scope thereof. Therefore, it is intended that the invention not be limited to the particular embodiment(s) disclosed, but that the invention will include all embodiments falling within the scope of the appended claims.
This application is a continuation of U.S. application Ser. No. 12/602,379 entitled “DEACTIVATION RESISTANT PHOTOCATALYST AND METHOD OF PREPARATION”, filed Nov. 30, 2009, which claims the benefit of PCT Application No. PCT/US2007/012882 filed May 31, 2007, entitled “DEACTIVATION RESISTANT PHOTOCATALYST AND METHOD OF PREPARATION”.
| Number | Date | Country | |
|---|---|---|---|
| Parent | 12602379 | US | |
| Child | 12627981 | US |
