AU657020B2 - Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brines - Google Patents
Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brines Download PDFInfo
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- AU657020B2 AU657020B2 AU30341/92A AU3034192A AU657020B2 AU 657020 B2 AU657020 B2 AU 657020B2 AU 30341/92 A AU30341/92 A AU 30341/92A AU 3034192 A AU3034192 A AU 3034192A AU 657020 B2 AU657020 B2 AU 657020B2
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- B60H3/00—Other air-treating devices
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- B60H3/0608—Filter arrangements in the air stream
- B60H3/0633—Filter arrangements in the air stream with provisions for regenerating or cleaning the filter element
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- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8659—Removing halogens or halogen compounds
- B01D53/8662—Organic halogen compounds
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- B01J19/123—Ultraviolet light
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- B01J35/00—Catalysts, in general, characterised by their form or physical properties
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- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/0215—Coating
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- B01J37/02—Impregnation, coating or precipitation
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- B60H3/00—Other air-treating devices
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion
- F01N3/2086—Activating the catalyst by light, photo-catalysts
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- B01J21/00—Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
- B01J21/18—Carbon
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- B01J2208/00—Processes carried out in the presence of solid particles; Reactors therefor
- B01J2208/00008—Controlling the process
- B01J2208/00017—Controlling the temperature
- B01J2208/00106—Controlling the temperature by indirect heat exchange
- B01J2208/00168—Controlling the temperature by indirect heat exchange with heat exchange elements outside the bed of solid particles
- B01J2208/00176—Controlling the temperature by indirect heat exchange with heat exchange elements outside the bed of solid particles outside the reactor
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- B01J2208/00008—Controlling the process
- B01J2208/00017—Controlling the temperature
- B01J2208/0053—Controlling multiple zones along the direction of flow, e.g. pre-heating and after-cooling
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- B01J2208/00592—Controlling the pH
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- B01J2219/18—Details relating to the spatial orientation of the reactor
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- B60H3/00—Other air-treating devices
- B60H3/06—Filtering
- B60H2003/0675—Photocatalytic filters
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- B60H2003/0691—Adsorption filters, e.g. activated carbon
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- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/30—Capture or disposal of greenhouse gases of perfluorocarbons [PFC], hydrofluorocarbons [HFC] or sulfur hexafluoride [SF6]
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Abstract
The invention relates to a process and devices for carrying out the process for purifying gases, exhaust gases, vapours and brines which are contaminated with undesirable chemical substances or are mixed with these at relatively high concentrations, by photocatalytic reactions which take place on the surface of catalysts. The catalysts (1) are situated in a fixed bed or a fluidised bed on catalyst supports. In the fluidised bed, the catalysts themselves can act as catalyst support. Catalyst supports and catalysts are situated in a closed system through which the substrate to be purified is passed. In the fixed-bed catalyst principle, the catalyst support/catalyst system continuously or discontinuously passes through a wash zone (12) for washing off the mineralisation products formed. The reaction is induced by photons of short-wave light of a wavelength between 250 and 400 nm. <IMAGE>
Description
7 0 S F Ref: 228780 I rt
AUSTRALIA
PATENTS ACT 1990 COMPLETE SPECIFICATION FOR A STANDARD PATENT
ORIGINAL
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Nai;e and Address of Applicant: Franz Dietrich Oeste Steinbergstr.4 D-6309 Munzenberg 2
GERMANY
Robert Aalbers Bramweg la Arnheim THE NETHERLANDS Olga geb Leye Dietrich 0.Hahnstr.2 D-6115 Munster
GERMANY
Actual Inventor(s): Address for Service: Invention Title: Franz Dietrich Oeste, Robert Dietrich Aalbers, Olga geb Leye Spruson Ferguson, Patent Attorneys Level 33 St Martins Tower, 31 Market Street Sydney, New South Wales, 2000, Australia Method and Apparatus for Removing Undesirable Chemical Substances from Gases, Exhaust Gases, Vapors, and Brines The following statement is a full description of this invention, including the best method of performing it known to me/us:- 5845/4 _i
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o 4 4 .r 4444 *1 4 4t 1C be b *4L~ 4*4 44I *4 4I -1- Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brines.
The present invention relates to a method and apparatus for purifying gases, exhaust gases, vapors, and brines, which are contaminated with undesirable chemical substances or contain high concentrations of these substances, by means of photocatalytic reactions occurring on the surface of catalysts.
The catalysts are situated on catalyst carriers in a fixed bed or in a fluidized bed. In fluidized beds, catalysts themselves can serve as catalyst carriers. The substrates to be purified are fed through a closed system which contains the catalyst carriers and catalysts.
In the fixed-bed catalytic method, the catalyst carrier/catalyst system continuously or discontinuously passes through a washing zone to remove the generated mineralization products. The reaction is induced by shortwave photons of wavelengths between 250 and 400nm.
In Environmental Sci. Technol. Vol. 17, No. 10 (1983) 828-31, for example, a reaction is described in which chloroform is degraded in an aqueous suspension of titanium dioxide by photoassisted heterogeneous catalysis.
Chloroform is a main by-product occurring in the disinfecting chlorine treatment of drinking water and alsc for example, water in swimming pools.
Chloroform is ascribed :rcinogen characteristics.
This method is applicable to aqueous suspensions with high particle content, known as slurries. A disadvantage of this method is the production of hydrochloric acid, which must be removed from the system.
European Patent Application 89100265.1 discloses a method and apparatus for the 2, removal of hydrogen sulfide from exhaust gases using a titanium dioxide catalyst applied on the surface of a honeycomb support of activated charcoal, and ultraviolet radiation.
The activated charcoal adsorbs odorous compounds, such as H 2 S and scatoles, which are degraded by ultraviolet light. The method is a selective method and has the disadvantage that only part of the total surface can be utilized for the reaction.
In DOS 40 23 995.0, a method is disclosed in which pollutants are photocatalytically mineralized by a fixed-bed catalyst which is moved relative to the photon source.
Compared to other methods for the destruction of pollutants, such as incineration, this method has the advantage that it does not create additional environmental pollutants.
These occur in incineration when auxiliary fuel is required, which usually results in the production of carbon dioxide.
22 8 -2- The method described in the cited DOS patent does not require auxiliary fuel, even when the pollutant occurs in very low concentrations, and is carried out at relatively low temperatures. Liquid or solid mineralization products such as phosphoric and arsenic acid, however, can accumulate on the photocatalyst if pollutants are continually employed which, in addition to carbon, hydrogen, oxygen, and nitrogen, contain, e.g., halogens, sulfur, phosphorus, or arsenic, as well as pollutants and other wastes consisting solely of these latter elements. The low reaction temperature, generally below does not allow these substances to evaporate. As a result, the photocatalytic function is increasing inhibited, and the reaction finally stops completely.
There are several known methods for removing pollutants and contaminants from exhaust gases and other media in which they are undesirable.
These include purely physical methods such as adsorption or absorption, or purely chemical methods such as chemisorption or incineration.
These methods, however, are frequently unsuitable for mineralizing or removing 15 complicated chemical compounds, such as sulfur hexafluoride, by economically or ecologically acceptable means. These methods have other disadvantages as well.
Physical sorption methods are limited by sorbent capacity. The loaded sorbent must either be disposed of, frequently as hazardous waste, or be desorbed, a process requiring large amounts of energy. The alternative incineration methods, on the other hand, 20 frequently lead to high expenditures for cleaning the exhaust gases for the pollutants and of the auxiliary fuel. The normally high incineration temperatures result in extremely high energy expenditures if the incineration warmth is not utilized All of the stated methods and apparatus in the art have certain disadvantages in their scope of application, service life, and the resulting total space-time yield, significantly i 25 reducing their cost-effectiveness.
0 Taking the shortcomings of other methods into consideration, it is the object of the present invention to provide a method and apparatus for carrying out the invention which circumvent the stated disadvantages, are more universally applicable, allow the resulting products to be easily removed from the system, and allow the mineralization of even difficult substances, such as inert halogen-carbon compounds, halogenated hydrocarbons or SF 6 The object of the present invention is realized by a method for the purification of gases, exhaust gases, vapor, and brines, contaminated with or containing undesirable chemical substances, by meas of photocatalytic reactions occurring on the surface of catalysts, wherein the substrate to be purified is fed through a physically closed system consisting of: 22 1 7( 0 sp -3a) a catalyst carrier with a high specific surface relative to the material used, which is long-term resistant to chemical corrosion and shortwave light, and which shows the mechanical stability needed for mobile mechanical parts; b) a catalyst applied to the catalyst carrier and consisting of at least one oxide and/or mixoxide with semiconductor behaviors mixed and/or loaded with a metal of the platinum series of the VIII group of periodic table of chemical elements; c) a catalyst applied to the catalyst carrier and consisting of at least one element of the lanthanides, actinides, and the IIIb group of the periodic table of chemical elements; d) at least one source of shortwave light of wavelength from 250 to 400nm, as a photon source; e) at least one washing zone for the catalyst carrier in accordance with on which catalysts are applied in accordance with b) and through which the catalyst carrier is transported and treated with polar solvents.
The catalyst carriers consist of mats, knitted or comparable wovens or nonwovens, 15 preferably in packets of stainless steel, titanium, tantalum, niobium, zirconium, hafnium, or metals of the VIII group of the periodic table of chemical elements, such as palladium or platinum. The surface of the catalyst carriers is roughened in order to increase the surface area and to improve the adhesion of the applied catalysts. The surface is roughened mechanically and for chemically-oxidatively. Examples for chemical roughening are acidic etching and for oxidative roughening annealing in an oxidative medium. The catalyst carrier packets or bundles are fixed in frames, on glass plates or similar apparatus, which consist of noncorroding materials and are resistant to shortwave light.
*99 Porous materials in tubes, for example, can be used as catalyst carriers as well. The catalyst carriers can consist of thick porous tubes or porous sheets. The porous sheets can be joined to form sheet systems as in heat exchangers.
In special cases, particularly in cases of low oxidative media, the catalyst carrier can consist of porous carbon or carbon fibers. Porous ceramics with zeolite structures or closed cell organic or inorganic polymers or polycondensation materials can be used as catalyst carriers as well.
In the method of the present invention, the catalyst carriers occasionally serve as catalysts themselves, metals containing partially oxidized titanium or zirconium or etched precious metals containing platinum or palladium. Partilly oxidized and etched metals have a very high specific surface and are therefore surface-active.
22710op 4- Catalysts are applied to the catalyst carriers and consist of semiconductor oxides mixed and/or loaded with a metal of the platinum series of the VIII group of the periodic table of chemical elements.
The oxides are of the formula: M2Ox, and M1M2Ox, where
M
1 elements of the Ia, IIa, IIb group of the periodic table M2 Ti, Zr, Hf, V, Nb, Ta, and those of the IIIB group such as yttrium and scandium.
The platinum series consists of primarily of palladium, platinum rhodium, and ruthenium.
x means a stechiometric or understechiometric value.
When chemical compounds are used which are extremely difficult to degrade, SF 6 or halogen-carbon compounds containing various halogens, an additional catalytic component is added to the catalytic system consisting of a salt, usually as chlorides of a lanthanide and/or an actinide element. The chlorides are converted to oxides and applied to the catalyst carrier.
The degradation reaction employed in the method of the present invention is induced by shortwave light usually supplied by low-pressure quartz lamps. Normally, light sources with a wattage between 200 and 1000W are used, depending on the size of the purification apparatus and the geometry of the light sources. The use of several light sources of low wattage is preferable to the application of a few light sources of high wattage, mainly to avoid heat build-up within the purification unit.
The method of the present invention can be employed not only in fixed-bed but also in fluidized-bed catalytic methods as well. In fluidized-bed methods, the catalyst is suspended in the reaction medium. Fluidized-bed catalysis has the advantage over fixed- 25 bed catalysis that higher concentrations of catalytic particles per unit of bed volume can be achieved. The catalytic fluidized bed, however, requires a relatively constant air or I, :gas flow through the fluidized particle bed. Occasionally, the flow rate of the reaction medium may be too high.
In these cases, particle mobilization is achieved by inducing vibrations in all or some of the fluidized-bed catalyst carriers. This is achieved by inducing vibrations inductively or piezoelectrically and is independent of the direetio: of flow which may be in or against the direction of acceleration under normal gravitational conditions or in a centrifuge.
To reduce noise emission, the vibrations within the fluidized bed may also be stimulated by an ultrasonic transmitter. When the flow is conducted horizontally over or through a particle bed surface, it is possible to deposit the bed coating as a continuous surface.
The vibratory bed has an advantage over the fluid-dynamically stimulated fluidized bed in that the requirements placed on particle fractionation are less stringent. If the catalytic 2297180p particles are at 1Vt artially on ferromagnetic catalyst carriers, moving lines of magnetic flux may be used as an additional particle stimulation method for mobile beds.
The movement of the lines of magnetic flux forces the particles of the catalytic bed to constantly rearrange themselves and, consequently, continuously present new surface areas to the photons.
The catalyst carrier and catalytic kIsad are continuously or discontinuously washed to regenerated the catalyst, as in the fixed bed catalytic method. Washing is conducted with polar solvents, preferably with water. The reactivation of the catalysts is improved if the washing medium contains oxidizing substances, for example, H202 or ozone. The catalysts are washed according to various process principles. For example, the catalyst czariers and catalysts are bathed, or dipped in a bath, or sprayed and centrifuged. In most cases, the substances to be removed are highly soluble, inorganic compounds.
If the mineralization is unfavourable, due to the composition of the substrate's contamination, the coating of the catalyst may be less soluble. In these cases, but also to generally accelerate mineralization, an aid, such as water vapor, ammonia, or liquid ammonia, may be added to the purification substrate.
The washing of fluidized catalysts is best conducted by exchanging the catalyst batch.
:Fluidized-bed catalytic methods are preferably employed when gases occur as sole mineralization products.
20 When the substrate gas consists, for example, of pure gas, air, oxygen-enriched air, and polluted water is sprayed into the substrate gas, the method becomes a purification method for liquid substances, in a reversal of the substrate admission in the purification method of the present invention.
In all, the method of the present invention is the method of choice for the special requirements of substrates which are to be purified.
A further object of the present invention was to provide apparatus with which the method may be carried out.
This object was realized by apparatus for carrying out the various applications of the method as described, the apparatus consisting of the following principal components: f) a closed housing of a corrosion-resistant material, equipped with inlet and outlet nozzles for the substrate and product of the method, as well as with bearings and clamps for the catalyst carriers and catalysts, and with a source of shortwave light; g) a frame to hold the catalyst carriers and catalysts; 221710p -6h) an apparatus to move the catalyst carriers and catalysts within the housing in accordance with f); and i) at least one source of shortwave light to the wavelength range from 250 to 400nm.
Except for the fluidized-bed method, the housing according to f) contains a cavity for the bathing liquid, which is equipped with inlet and outlet nozzles for the bathing liquid.
The catalb .,ntaining carrier is held in a frame, cage, or is otherwise secured, and moved through the bath in the cavity in such a way that, as a minimum, the entire carrier passes through it.
Alternatively, the washing of the catalyst may be conducted by a spraying method. The spray drips into the cavity, from which it is removed or returned to the process by recirculation.
I Due to the long-term effectiveness of the catalysts, washing by bath or spraying may be conducted in intervals.
The frame g) frequently is a cylindrical body with a central axle, a cavity surrounding the axle, followed by a round container, which may be subdivided into pockets and U "which is connected to the axle on both sides, resulting in a closed container 14 whose outer 62 and inner 63 cylinder casings are constructed in such a manner that they are easily permeable for gases and can easily contain and secure the catalyst carriers and catalysts.
The frame holding the catalyst carriers and catalysts may be constructed in various geometric forms, for example, a square object in a packet which travels up and down within the hous;ig in accordance with g) and is thereby submerged in the washing liquid.
When applying such variations of the method, it must be guaranteed that the purification process is interrupted during the washing process or that multiple systems are in service so the substrate to be purified is fed to an available purification unit by synchronized switching.
Frames are not required in the fluidized-bed method. The catalyst carriers and catalysts are suspended within the container and require a supporting base plate or drum which must be permeable for gases but impermeable for particulate matter.
The method can be conducted in reductive as well as in oxidative media, for example, when purifying extremely inert chlorofluorohydrocarbons. These compounds are best mineralized under oxygen-free conditions and in the presence of H2S, 'CS 2 COS or 227110 -7mixtures thereof. The presence of w-ter and/or ammonia also promotes the reaction.
Other reductive agents which helps to eliminate halogens, are for example, dithiols, mercaptans, thiophenols and their alkali salts, sodium sulfide, and sodium polysulfide, which are introduced to the process as gases or, for example, as aqueous solutions.
By reversing these conditions, these sulfur compounds, if occurring as unwanted pollutants, can be eliminated by the method of the present invention. This is especially important, since these compounds are extremely odorous.
Many gases contain significant amounts of the covalently bound pollutants as aerosols.
In a variation of the method of the present invention, precipitation of these components can be promoted by connecting the catalyst fixed bed to a voltage differential.
Depending on the geometry of the fixed bed, the backplate electrode may be either the housing f) itself, or appropriately positioned wires, or even an additional catalyst fixed bed, as shown in Fig. 3.
I Surprisingly, the new method functions even if the aqueous phase, the bath or the washing liquid used to spray the catalyst, is polluted with organochemical substances.
The pollutants are adsorbed from aqueous solution and adhesively bound by the catalyst carrier and the catalyst. Even oil films on the surface of the water or substances S* dissolved in the aqueous solution, for example, are adsorbed by the catalyst fixed bed, appear in the gas phase, and are mineralized under the influence of the photons. This variation shows the applicability of the method for purifying extremely polluted waste water, which would be difficult by any other means.
Examples of the apparatus required for carrying out the method are illustrated in Figures lto7.
Fig 1. shows a standard apparatus. The hermetic enclosure of the reaction chamber 4:6*64 25 11 by the bath 12 and the side wall of the cylindrical container 14 forces the substrate to travel through the photon-irradiated 7 catalyst fixed bed 1. This is also where photocatalytic mineralization of undesirable substrate components occurs. The purified product leaves the purification unit 15 via the hollow axle 5. The catalyst fixed bed and the catalysts are washed in bath 12 and freed of minerals, which are removed with the washing liquid via nozzle Fig 2. shows the same apparatus in a vertical cross section along the middle axis.
Fig 3. shows a variation of the apparatus for the purification of covalently bound pollutants in aerosols. Purification is best conducted with an electric field as described in Example 8.
221710op -8- Fig 4. shows a variation of the apparatus for pollutants which are extremely difficult to eliminate. The apparatus is designed such that purification is conducted in two stages.
The first purification stage occurs between chamber areas 34/51, and the second stage occurs between chamber areas 42/52. The method is described in detail in Example Fig 5. shows a vertical cross section of the apparatus of Fig. 4.
Fig 6. shows a variation of the apparatus in which the washing liquid is admitted through the same inlet as the substrate to be purified. The catalyst carrier and catalyst are washed by spinning off the washing liquid as described in Example 9.
Fig. 7 shows an apparatus which uses fluidized-bed catalysts.
The applications of this new method are extremely diverse. The fixed-bed catalyst method is used in households for air purification as well as for flue gas dust collectors.
In vehicles, it is used for purifying circulated air and exhaust gases. In public buildings, schools, parking garages, and hospitals, it is used for purifying circulated air and emissions. Fixed- and fluidized-bed catalytic methods are also employed in several other S 15 sectors, for example, in paint factories and paint shops, in glue factories and in gluing, and in the production of printing inks and in printing to remove solvent and softener vapors. They are also used in the chemical and pharmaceutical industries, in refineries, and in coking plants to remove all types of pollutants, employing as required a variation of the method of the present invention. They are also used for occupational safety, for 20 example, in welding. Other applications are the decontamination of ground water and soil by abandoned pollutants or following accidents. Further applications are the destruction of chlorofluorohydrocarbons, PCBs, or other environmental poisons, dangerous by-products of semiconductor production, such as AsH3, SiCI 4 SiHCl 3 SiH 4 SF6, MoF6, the flue gases of viscose production, which contain CS 2 and H 2
S,
S 25 the black liquors occurring in cellulose production, and waste waters in electroplating S" shops, tanneries and pesticide pollution.
The destruction of gases for chemical warfare, such as LOST, or nerve gases which Scontain phosphorus are additional fields of application. The method is also called for in clean-room technology, since a precleaning step would significantly reduce even residual traces of micro-particles. The new method is a significant contribution to solving environmental pollution problems and is extremely energy-saving and cost-effective.
The following examples will demonstrate some of the capabilities of the method and its apparatus.
221700*o k l
_I_
0* *e 4 4 4444 or 4 1.
2.
3.
4.
6.
7.
8.
9.
11.
12, 13.
14.
15.
16.
17.
18.
19.
20.
21.
22.
23.
24.
26.
27.
28.
29.
31.
32.
33.
34.
36.
37.
38.
-9- List of reference catalyst fixed bed 39.
axial face seal 40.
motor 41.
strap or gear disk 42.
hollow axle 43.
substrate inlet nozzle 44.
shortwave lamp photon source 45.
washing liquid inlet 46.
washing liquid outlet 47.
bath outflow 48.
gas phase chamber 49.
catalyst washing bath 50.
isolating float 51.
cylindrical catalyst bed carrier 52.
apparatus housing 53.
pure product outlet nozzle 54.
substrate to be purified 55.
spray nozzles 56.
catalyst fixed bed, Fig. 3 57.
catalyst carrier cylinder 58.
photon source, Fig. 3 59.
rotating main axle 60.
aperture to 2nd purif. stage 61.
washing liquid outlet 62.
housing, Fig. 3 63.
negative voltage source 64.
positive voltage source 65.
isolating plastic sleeve 66.
sliding contact 67.
sliding contact 68.
pure product outlet 69.
pockets for catalyst fixed bed 70.
substrate inlet 71.
crude gas chamber, 1st purif. stage 72.
73.
74.
aperture to 2nd purif. stage 75.
seal 76.
numbers catalyst washing bath washing liquid inlet washing liquid outlet siphon crude gas chamber, 2nd purif. stage mineralization aid inlet stirring rotor photon source photon source pure product outlet centering drive rollers drive transmission levelling lock pure gas chamber, 1st stage pure gas chamber, 2nd stage bath housing, Fig. 4 and supporting axle plain bearing outer cylinder casing inner cylinder casing middle catalyst bed substrate inlet nozzle hollow axle catalyst beds quartz glass plates UV lamps pure product chamber pure product outlet apparatus outer casing apparatus bottom washing liquid outlet vibrating base plate 4.
4r 0 4*r 220780*p List of reference numbers cont...
77. mesh bottom plates (frits) 78. catalyst fluidized bed 79. quartz glass plate crude gas inlet 81. pure gas outlet Example 1 Preparation of the catalyst carrier A three-dimensional, knitted wire mat of stainless steel with a layer thickness of 50mm is cut into strips of 150mm width and 1000mm length. The mesh is ca. 10mm. The strips are used to form a hollow cylinder with the following dimensions: outer diameter ca.
30cm, inner diameter ca. 20cm, cylinder height ca. 15cm. The mat is held in shape by meshed stainless steel wires. The cylinder is then blasted with grey cast iron blasting 10 shot, mesh 0.2 to 0.4mm, until the surface of the wire mat is well roughened, recognizable by the delustering of the wires. Following this pretreatment, the diameter of the knitted wires is ca. 0.2mm. The wire mesh is then washed and thoroughly dried.
The wire mesh is then dipped into a solution of soluble sodium, density 1.4kg/l, and thoroughly wetted.
Short activated charcoal fibers with an average length of 1.0 to 3.5mm, which are best produced by cutting fibrous webs of activated charcoal, are added to a 5% aqueous solution of citric acid. The charcoal fibers sediment completely in the citric acid solution and are then removed by decanting and filtration. The fibers are then dried to a constant weight at 70°C. The fibers are shaken through a sieve onto the wire mat, which has S- 20 been wetted with the soluble sodium solution, until the surface of the wires is covered Swith the short charcoal fibers as completely as possible. Prepared in this manner, the wire mat is then sprayed uniformly with a 5% aqueous solution of soluble sodium, followed by a 5% aqueous solution of citric acid. It is then dried to a constant weight at i 110°C. This method produces a thin silicate layer on the flock costi.g of charcoal fibers.
Subsequently, the wire mat is repeatedly dipped into a water bath to remove all soluble salts. The wire mat is then dried to a constant weight at 700C.
Preparation of the catalyst A suspension is prepared containing: 228780p -11titanium dioxide powder, rutile type, mesh smaller tharn 0.1 mm ethyl titanate, 3% bentone s- .;len in xylol palladium, metal colloid rhodium, metal colloid and 81.0% xylol Depositing the catalyst on the catalyst carrier The catalyst suspension is deposited on the catalyst carrier by spraying or dipping and is dried at a temperature between 20°C and 50°C and a relative humidity of 50% to After the catalyst carrier and catalyst have been prepared as described, they are built into the apparatus components shown in Figs. 1 and 2, container 14.
t l Procedure
I
Container 14 with catalyst carrier and catalyst 1 is mounted on a rotatable axle supported by bearings 61 in a closed housing 15. Catalyst carrier and catalyst form the catalyst fixed bed 1. The cylindrical container 14 is closed on both sides. The flow of substrate to bi purified enters the purification unit (Figs. 1 and 2) of housing 15 via inlet nozzle 6. Since housing 15 is hermetically sealed, the substrate can reach the hollow axle 5 only by traversing the catalyst fixed bed 1. The hollow axle 5 is also the outlet nozzle through which the substrate leaves the purification unit as a purified product.
During the reaction, the catalyst fixed bed 1 is activated by several 200W low pressure 20 quartz lamps 7. The cylinder (container) 14 is continually rotated on cylinder axle during the work phase. The axle 60 is driven by motor 3 via hollow axle 5 and strap or gear disk 4. During the work phase, the rotation dips the complete casing of the catalyst fixed bed into bath 12, which in this case is a water bath and is situated in the lower section of housing 15. The wash water enters the bath by inlet 8 at a rate of ca. 2 to 51/h.
After it is loaded with the mineralization products, it is removed from the bath via outlet 9. In the reaction area of the quartz lamps 7, the surface of the bath is covered with isolating floats 13 to minimize evaporation and heating. Container 14 is turned at a speed of ca. 0.5 to 1.0 times per hour. Tap water, but preferably water from an ion exchanger, is used as the washing liquid.
The process operates as follows: 22B7809p -12- An air stream is adjusted to a relative humidity of ca. 90% by feeding it th:rough a tank of cooled water at a rate of 0.3 1/s. At a rate of 0.1 1/s, an additional stream of air is fed through a 2 liter washing flask roughly half-filled with a solution of various biocide substances. The biocide solution is of the following composition: 30% profenofos (O-ethyl-S-propyl-O-(2-chloro-4-bromphenyl)-thiophosphate;
C
1 1
H
15 BrCIO 3
PS),
chlorofos (0,0-dimethyl-2,2,2-trichloro-l-hydroxy-ethanephosphate;
C
4
H
8 C 130 4
P),
cacodyl oxide (bis(dimethyl arsyl)oxide; As 2
(CH
3 4 0), 25% demeton-S (O,O-diethyl-S-(ethyl thio)ethyl thiophosphate; C8H 19 0 3 PS2), fluoro acetic acid-n-butyl ester (C 6
H
1 1 F0 2 The two air streams are mixed with a static mixer and fed through the apparatus shown in Figs. 1 and 2. A defined aliquot of the gas stream fed through the catalyst fixed bed is diverted for analysis and burned in an oxyhydrogen gas flame. The resulting gas is 15 condensed in a quartz cooler such that the condensate drips from the cooler into a diluted hydrogen peroxide solution. The fluoride, bromide, sulphate, phosphate and arsenate content of the hydrogen peroxide solution is analyzed at two-hour intervals. The solution contains hydrogen peroxide and a small amount of potassium iodide.
Even after the experiment was conducted continually for two weeks, none of the ions S 20 mentioned above was detected in the hydrogen peroxide solution.
Exampl e 2 (Comparative example) 44 The process is conducted exactly as described in Example 1, except that the catalyst is not washed. Pollutants were detected in the emissions after only 24 hours reaction time.
I Example3 The process is conducted as described in Example 1, but the catalyst is washed not by bathing but rather by spraying the catalyst and catalyst carrier from the inside of container 14. The washing liquid is removed through outlet 10. Container 14 is rotates at a speed of 300 to 1500 rpm during the washing method. The washing is conducted discontinuously at intervals of 2 to 24 hours depending on the pollutant content of the substrate to be purified The resulting emissions are of the same quality as in Example 1.
Example4 228780p 13- The process is conducted exactly as described in Example 1, except that the catalyst is washed discontinuously. Bath 12 is filled for 15 minutes every two hours. The washing liquid is then removed. The same good results were achieved as in Example 1.
ExampleS Preparation of the catalyst carrier and catalyst A 20mm thick, stainless steel knitted mat is cut into strips of 38cm length and 4cm width and roughened by corundum streams. The roughened stainless steel strips are treated with soluble sodium as in Example 1.
short aluminium oxide fibers with an average length of 1 to 3mm and a diameter of 0. lmm are stirred into a solution of 75g thorium tetrachloride, 30g cerium trichloride and 15g yttrium trichloride in 3 1 of water. The solution is then neutralized by adding sodium hydroxide. The chlorides are converted into hydroxides and precipitate on the S surface of the aluminum oxide fibers. The applied fibers are removed by filtration, neutralized by washing, and dried.
The dry fibers are fluidized by a vertical air stream and the stainless steel knitted mat, which was wetted by treatment with soluble sodium, is flock coated by dipping into the short fiber fluidized bed. A high fiber density is achieved by applying a relatively high voltage of 5kV to the stainless steel knitted strips during flock coating. Immediately thereafter, the coated strips are dried to a constant weight in a C0 2 atmosphere at room temperature. They are then dried to a constant weight in a nitrogen atmosphere while the temperature is gradually increased to 4000C. This temperature is maintained for two hours. The resulting strips are freed of alkali carbonates by washing and dried.
Subsequently, the prepared catalyst carrier is coated and fixed with palladium- and rhodium-doped titanium dioxide, as described in Example 1.
25 The resulting catalyst carriers and catalysts are mounted in the 64 pockets 32 of the catalyst carrier cylinder 20 as shown in Figs. 4 and 5. Cylinder 20 is then mounted in housing Cylinder 20 is mounted in chamber housing 55 such that sections of the cylinder are simultaneously in both of the chambers while the cylinder rotates. Cylinder 20 divides each of the two chambers 34/51 and 42/52 into tw( sections, the substrate section and the product section.
Cylinder 20 rotates counterclockwise at a speed of 0.5 rpmn and is driven eccentrically by the interconnected supporting rollers 48.
Procedure 2 2 87809p 14- Nitrogen containing 1000 ppm sulfur hexafluoride, 5000 ppm carbon disulfide, 10000 ppm ammonia, and 20 g/m 3 water vapor is fed into the chamber 34 via substrate inlet nozzle 33 at a rate of 0.3 1/s and a temperature of 23 C.
The quartz lamps 45 and 46 on both sides of the chamber are turned on.
The photon emission maximum is between 300 and 400nm.
The gas is fed through catalyst bed 62, where practically all pollutants are converted to elementary sulfur, ammonium fluoride, and carbon dioxide.
The resulting sulfur and ammonium fluoride remain on the catalyst.
The gas is then fed through aperture 37 into chamber 42 where, at a temperature of 20°C, it is mixed with air which enters by inlet 43 at a rate of 0.3 1/s and whose relative humidity has been adjusted to 100% at a room temperature of The gases are stirred by rotor 44.
Without a change in photon conditions, the gas mixture is fed through catalyst bed 62 into chamber 52.
15 The gas reaching chamber 52 does not contain sulfur dioxide or any other pollutants.
S' Residual pollutants, as well as the elementary sulfur on the catalyst, are converted to ammonium sulfate and ammonium hydrogen sulfate in the catalyst fixed bed of chamber 'areas 42/52. The purified product is removed from the purification unit by outlet 47.
The catalyst bed is washed continuously while moving through bath 63. The washing liquid enters upper section 39 of the bath by inlet 40 at a rate of 2 I/h, is fed through the S, catalyst bed where it removes mineralization products and is collected in lower section s 53 of the bath.
The washing method removes mineralized salts, such as fluorides and sulfates. The resulting washing liquid is removed from the purification unit by siphon 41. Leveling 25 locks 50 are regulated by the height of the siphon.
The ammonia content of the washing liquid is monitored via the pH-value, which varies between 6.5 and The seals 38 minimize gas leakage between the chambers.
Waste water processing Milk of lime is added to the waste water. The resulting sulfates and fluorides precipitate as gypsom arid fluorspar.
Subsequently, the waste water is stripped in a packed column using air in a counterflow system. The stripping air, which contains ammonia, is recycled via aperture 37 and is reintroduced to the process in chamber 42.
The precipitated calcium salts are removed by filtration and disposed of. The filtrate can be used as service water.
228780sp In this manner, extremely dangerous chemical substances are converted to harmless mineral salts.
Example6 As in Example 5, but with the following substrate composition: 500 ppm bromtrifluoro methane (halon), 200 ppm difluoro-dichloro methane instead of sulfur hexafluoride, and 5000 ppm 11 2 S instead of carbon disulfide.
More than 95 of the covalently bound halogens are mineralized to halogenides.
The waste water filtrate cannot be used as service water, since it contains calcium chloride and bromide.
E xaminpIe 7 As in Example 5, except that a knitted mat of titanium wire, preferably roughened, and of less than 0.5mm diameter is used instead of a stainless steel mat.
4. 0 The knitted mat is annealed in oxygen, resulting in a titanium dioxide layer on the surface of the wires, which supplies the required catalytic properties in this process.
Subsequently, the wire mat is doped with one or a mixture of the platinum metals and/or oxidized compounds of the elements or their mixtures from the lanthanide group or o yttrium or the actinide group, leading to the same good results.
Many gases contain significant amounts of the covalently bound pollutants as aerosols.
For the precipitation of these components, it is advantageous to connect the photocatalyst fixed bed to a voltage differential. Depending on the geometry of the fixed bed, the 0 *backplate electrode may be either the housing itself, appropriately positioned wires, or even an additional catalyst fixed bed.
Fig 3 shows the geometry of three catalyst fixed beds 19, 65, which rotate around a common axle 22 within housing 25. Both external catalyst beds are connected electrically with conductive metal axle 22 and, via sliding contact 29, positive voltage source 27.
Central catalyst bed 65 is isolated from metal axle 22 by plastic sleeve 28 and receives a negative charge via sliding contact 30 from voltage source 26. Two photon sources 21 are mounted rigidly between rotating catalyst beds 19, Spray nozzles 18 enrich the substrate, which enters the purification unit via 17, with an aerosol of washing liquid. The rotational speed of the catalyst beds is variable between 228700@mp 'Is 16and 500 rpm. In intervals, rotational speed is increased to maximum to spin off washing liquid during washing. Subsequently, the spun-off washing liquid is removed from the apparatus by outlet 24. The purified gas is removed by outlet 31.
5000 to 30,000 V is the best voltage range for stripping aerosols.
The catalyst carriers are prepared according to Examples 1 and Example9 Fig. 6 shows a further variation of the method using aerosols. The substrate polluted gas is fed through inlet 66, hollow axle 67, and catalyst beds 68.
Spray nozzle 18 enriches the substrate with an aerosol of washing liquid. The catalyst beds are mounted between disk-shaped, round quartz glass plates 69, which are securely fastened to the hollow axle. The hollow axle is permeable for gases in the catalyst bed section between the quartz glass plates.
:t The hollow axle and, consequently, the catalyst bed are turned by a motor and drive unit i-o ,o4, as in Example 8. UV lamps 70, the photon sources, are located between the catalyst S 15 beds. The purified substrate is fed into chamber 71 and removed from the unit as a pure product by outlet 72. A filled gas washer is mounted downstream of the purification unit to strip aerosols.
S°of The washing liquid aerosol aggregates and coalesces within the catalyst fixed bed, is o spun to wall 73 of the unit, collects in bottom section 74, and is removed from the apparatus by outlet SExample A variation of Example 9 is to secure the photocatalyst fixed bed by a tight, transparent housing. The catalyst is secured within glass capillaries. This is achieved by applying the catalyst to the glass walls or pores of the capillaries. When employing wide capillaries with diameters of ca. 1 mm and larger, the catalyst particles are applied by pouring. Previous etching improves the adhesion of the catalyst to the glass surface.
Examplell The apparatus can also serve as a waste water purification unit if, as in Example 9, the spray nozzle is fed with water to be purified and inlet 66 is fed with clean air.
228780op
Claims (33)
1. A method for purifying gases, exhaust gases, vapors and brines, which are contaminated with or contain undesirable chemical substances, by means of photocatalytic reactions occurring on the surface of catalysts, wherein the substrates to be purified are fed through a physically closed system consisting of: a) a catalyst carrier with a high specific surface relative to the material used, which is long-term resistant to chemical corrosion and shortwave light, and which shows the mechanical stability needed for mobile mechanical parts; b) a catiyst, which is applied to said catalyst carrier, and which consists of at least one oxide and/or mixoxide with semiconductor behaviours mixed and/or loaded with at least one metal of the platinum series of the VIII group of the periodic table of chemical elements; c) a catalyst, which is applied to said catalyst carrier, and which consists of at least one element of the lanthanides, actinides, and the IIIb group of the periodic table of chemical elements; d) at least one source of shortwave light of wavelengths from 250 to 400 nm, as a photon source; e) at least one washing zone for said catalyst carrier in accordance with on which catalysts are applied in accordance with b) and through which said catalyst carrier is transported and treated with polar solvents.
2. The method of claim 1, wherein said catalyst carrier consists of roughened wovens or nonwovens made of stainless steel, titanium, tantalum, niobium, zirconium, hafnium, or metals of the VIII group of the periodic table of chemical elements, whereby roughening is conducted mechanically or oxidatively, in the latter case resulting in a roughening thin oxide layer, and whereby said wovens and nonwovens are joined into packets and framed by noncorroding materials.
3. The method of claim 1, wherein said catalyst carrier consists of noncorroding, porous material.
4. The method of claim 1, wherein said catalyst carrier consists of carbon fibers or porous carbon material with a high specific surface.
The method of claim 1, wherein said catalyst carrier consists of ceramic material with zeolite structure. 22 8 780op
6. The method of claim 1, wherein said catalyst carrier consists of noncorroding closed-cell organic or inorganic polymeric or polycondensation material.
7. The method of any one of claims 1 to 6, wherein said semiconductor oxide is titanium dioxide and said precious metal is palladium or platinum, used in particle form with a high specific surface.
8. The method of any one of claims 1 to 6, wherein said semiconductor oxide is hafnium oxide or zirconium oxide and said precious metal is platinum or palladium, used in the modified form with a high specific surface.
9. The method of any one of claims 1 to 8, wherein said elements according to c) are used as chloride salts and are, after their conversion, applied as oxides.
The method of any one of claims 1 to 9, wherein a low-pressure quartz lamp is used as said light source.
11. The method of any one of claims 1 to 10, wherein said washing zone according to e) is passed through continuously or at time intervals, resulting in a ;15 complete wetting and washing of said catalyst carrier according to a) with said catalysts according to b) and c) per time interval.
12. The method of any one of claims 1 to 11, wherein said washing is conducted with water.
13. The method of any one of claims 1 to 12, wherein oxidizing chemicals are j 20 added to said aqueous solution.
14. A method for purifying gases, exhaust gases, vapors and brines, which are It contaminated with or contain undesirable chemical substances, by means of photocatalytic reactions occurring on the surface of catalysts, which method is substantially as herein described with reference to any one of Examples 1 or 3 to 11.
15. A method for photocatalytic mineralization according to claim 1, wherein mineralization of undesirable chemical substances is improved by adding mineralization aids to said substrate to be purified.
16. The method of claim 15, wherein ammonia is added to said substrate to be purified,
17. The method of any one of claims 1 to 16, wherein at least one element according to c) is applied in an amount equaling 0 to 15 weight percent of the total amount of catalyst used. 228780p i I I 19
18. The method of any one of claims 1 to 17, wherein said substrates to be purified are fed through a fluidized bed in a physically closed system consisting of: subitems and d).
19. The method of claim 18, wherein gaseous products are produced which do not undergo a washing-out method in the system.
The method of any one of claims 1 to 19, wherein said oxides according to b) have the following formulae: M 2 Ox and M 1 M 2 Ox, where M1 elements of the Ia, IIa and IIb group of the periodic table M 2 Ti, Zr, Hf, V, Nb, Ta, and elements of group IIIb, x an stechiometric or understechiometric value in relation to value of the M 1 and M 2 elements, and wherein the platinum series consists primarily of palladium, platinum, rhodium, and ruthenium.
21. The method of claim 20 wherein said elements of group IIIb are selected from yttrium and scandium.
22. A method for photocatalytic mineralization according to any one of claimils 1 to 21, which method is substantially as herein described with reference to any one of Examples 1 or 3 to 11.
23. An apparatus when used for carrying out the methods of any one of claims 1 to 9, comprising the following components: f) a closed housing consisting of corrosion-resistant material equipped with inlet and outle;: nozzles for said substrate and bearings and clamps for said catalyst carriers with catalysts and said sources of shortwave light; 'IT g) a frame to hold said catalyst carrier with said catalysts; 25 h) an apparatus for moving said catalyst carrier and catalysts in said housing according to and i) at least one source of shortwave light of wavelengths between 250 and 400 nm.
24. The apparatus of claim 23, wherein said housing according to f) contains a cavity for receiving a bathing liquid equipped with necessary inlet and outlet nozzles for said bathing liquid.
The apparatus of claim 23 or 24, wherein said frame with said catalyst carrier and catalysts according to g) is flexibly affixed within said housing according to t) in such a way that its entirety passes through said bath according to e).
26. The apparatus of any one of claims 23 to 25, wherein said housing according to f) contains a spraying apparatus for washing said catalyst carrier and catalysts, whereby said washing liquid returns into said bath and is recirculated for spraying.
27, The apparatus of claim 26, wherein said spraying apparatus is equipped with a time switch for interval washing,
28. The apparatus of any one of claims 23 to 27, wherein said frame according to g) is a cylindrical body with a central axle, a cavity surrounding said axle, followed by a [a:AWPU9R\I1AAAo0029:VGS r.l ~LCIICI' round container, which may be subdivided into pockets and which in connected to said axle on both sides, resulting in a closed container whose outer and inner cylinder casings are constructed in such a manner that they are easily permeable for gases and can easily contain and fix said catalyst carriers and catalysts.
29. The apparatus of any one of claims 23 to 27, wherein said frame according to g) is a square object in a packet which contains said catalyst carrier and catalyst and which travels up and down on vertical plain bearings within said housing according to g) and submerges in said washing liquid.
The apparatus of any one of claims 23, 24, or 29, wherein two or more units are employed and switching of the feed method is synchronized in such a manner that said method is not interrupted during catalyst washing.
31. The apparatus of any one of claims 23 to 29, wherein said frame according to g) consists of a plate which is permeable for gases when using said fluidized catalyst process for gaseous mineralization products.
32. The apparatus of any one of claims 23 to 31, consisting of several subchambers for said substrate reaction in multi-stage processes.
33. An apparatus for carrying out the methods of any one of claims 1 to substantially as herein described with reference to any one of Figs. 1 to 7. Dated 2 December, 1994 e Franz Dietrich Oeste Robert Aalbers Olga geb Leye Dietrich Patent Attorneys for the Applicants/Nominated Persons SPRUSON FERGUSON i 4( g *I IG:\WPUSt3PM3AAIO0219NGS Method and apparatus for removing undesirable chemical substances fr Im gases, exhaust gases, vapors, and brines. Abstract The present invention relates to a method and pertinent apparatus for purifying gases, exhaust gases, vapors, and brines, which are contaminated with undesirable chemical substances or contain high concentrations of these substances, by means of photocatalytic reactions occurring on the surface of catalysts. The catalysts are situated in a fixed or fluidized bed on catalyst carriers. In fluidized beds, the catalysts themselves can serve as catalyst carriers. The substrates to be purified are fed through a closed system which contains the catalyst carriers and catalysts. In the fixed-bed catalytic method, the catalyst carrier/catalyst system continuously or discontinuously passes through a washing zone to remove the generated mineralization 4 products. The reaction is induced by shortwave photons of wavelengths between 250 S 15 and 400 nm. The hermetic enclosure of the reaction chamber 11 by the bath 12 and the side wall of the cylindrical container 14 forces the substrate to travel through the photon-irradiated 7 catalyst fixed bed 1. This is also where photocatalytic mineralization of undesirable substrate components occurs. The purified product leaves the purification unit 15 via the hollow axle The catalyst fixed bed and the catalysts are washed in bath 12 and freed of minerals, which are removed with the washing liquid via nozzle Figure 1 2287800p A
Applications Claiming Priority (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE4142520 | 1991-12-21 | ||
| DE4142520 | 1991-12-21 | ||
| DE4241451A DE4241451A1 (en) | 1991-12-21 | 1992-12-09 | Methods and devices for cleaning gases, exhaust gases, vapors and brines from undesirable chemical substances |
| DE4241451 | 1992-12-09 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| AU3034192A AU3034192A (en) | 1993-06-24 |
| AU657020B2 true AU657020B2 (en) | 1995-02-23 |
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| Application Number | Title | Priority Date | Filing Date |
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| AU30341/92A Ceased AU657020B2 (en) | 1991-12-21 | 1992-12-21 | Method and apparatus for removing undesirable chemical substances from gases, exhaust gases, vapors, and brines |
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| Country | Link |
|---|---|
| EP (1) | EP0590202B1 (en) |
| JP (1) | JPH05337337A (en) |
| CN (1) | CN1076139A (en) |
| AT (1) | ATE142898T1 (en) |
| AU (1) | AU657020B2 (en) |
| CA (1) | CA2085758A1 (en) |
| DE (2) | DE4241451A1 (en) |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| EP0738539A1 (en) * | 1993-01-18 | 1996-10-23 | PCP-PHOTOCATALYTIC PURIFICATION GmbH | Process for cleaning gases, waste gases, vapours and water containing unwanted chemical compounds |
| EP0792687B1 (en) | 1994-11-16 | 2003-01-15 | Toto Ltd. | Photocatalytic functional material and method of production thereof |
| WO1996038212A2 (en) * | 1995-05-23 | 1996-12-05 | United Technologies Corp | Back-side illuminated organic pollutant removal system |
| DE69735209T2 (en) * | 1996-09-20 | 2006-09-21 | Daiken Chemical Co. Ltd., Osaka | PHOTOCATALYZER WITH ULTRA-FINE METAL PARTICLES, HIGH-FUNCTIONAL MATERIAL CHARGED WITH THE PHOTO CATALYST AND METHOD FOR THEIR PRODUCTION |
| NL1004961C2 (en) * | 1997-01-09 | 1998-07-13 | Dsm Nv | Monolith reactor. |
| IL121877A (en) * | 1997-10-01 | 2001-09-13 | Yissum Res Dev Co | Photocatalysts for the degradation of organic pollutants |
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| DE4023995A1 (en) * | 1990-07-28 | 1992-01-30 | Ruetgerswerke Ag | Purifying fresh and recirculated air in vehicle using photocatalyst - based on semiconductor in fixed stationary bed irradiated with UV light |
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| JP2691751B2 (en) * | 1988-10-14 | 1997-12-17 | 株式会社日立製作所 | Catalytic structure and method and apparatus for producing the same |
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| US5045288A (en) * | 1989-09-15 | 1991-09-03 | Arizona Board Of Regents, A Body Corporate Acting On Behalf Of Arizona State University | Gas-solid photocatalytic oxidation of environmental pollutants |
| WO1991009823A1 (en) * | 1990-01-04 | 1991-07-11 | Trustees Of Boston University | Photocatalytic process for degradation of organic materials in a vaporized or gaseous state |
-
1992
- 1992-12-09 DE DE4241451A patent/DE4241451A1/en not_active Withdrawn
- 1992-12-16 EP EP92121367A patent/EP0590202B1/en not_active Expired - Lifetime
- 1992-12-16 ES ES92121367T patent/ES2096013T3/en not_active Expired - Lifetime
- 1992-12-16 DE DE59207201T patent/DE59207201D1/en not_active Expired - Fee Related
- 1992-12-16 AT AT92121367T patent/ATE142898T1/en not_active IP Right Cessation
- 1992-12-18 CA CA002085758A patent/CA2085758A1/en not_active Abandoned
- 1992-12-21 MY MYPI92002356A patent/MY109975A/en unknown
- 1992-12-21 CN CN92115370A patent/CN1076139A/en active Pending
- 1992-12-21 JP JP4361827A patent/JPH05337337A/en active Pending
- 1992-12-21 AU AU30341/92A patent/AU657020B2/en not_active Ceased
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4892712A (en) * | 1987-09-04 | 1990-01-09 | Nutech Energy Systems Inc. | Fluid purification |
| DE4023995A1 (en) * | 1990-07-28 | 1992-01-30 | Ruetgerswerke Ag | Purifying fresh and recirculated air in vehicle using photocatalyst - based on semiconductor in fixed stationary bed irradiated with UV light |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH05337337A (en) | 1993-12-21 |
| CA2085758A1 (en) | 1993-06-22 |
| DE4241451A1 (en) | 1993-12-16 |
| DE59207201D1 (en) | 1996-10-24 |
| ATE142898T1 (en) | 1996-10-15 |
| ES2096013T3 (en) | 1997-03-01 |
| EP0590202A1 (en) | 1994-04-06 |
| AU3034192A (en) | 1993-06-24 |
| MY109975A (en) | 1997-10-31 |
| CN1076139A (en) | 1993-09-15 |
| EP0590202B1 (en) | 1996-09-18 |
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Legal Events
| Date | Code | Title | Description |
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| MK14 | Patent ceased section 143(a) (annual fees not paid) or expired |