AU710253B2

AU710253B2 - Enhanced adsorbent and room temperature catalyst particle and method of making and using therefor

Info

Publication number: AU710253B2
Application number: AU55516/96A
Authority: AU
Inventors: Bryan E Kepner; Mark L Moskovitz
Original assignee: M & K Patent Co Inc
Current assignee: Apyron Technologies Inc
Priority date: 1995-04-21
Filing date: 1996-04-17
Publication date: 1999-09-16
Anticipated expiration: 2016-04-17
Also published as: WO1996033013A3; NZ306840A; PL322886A1; ZA963056B; BR9608145A; WO1996033013A2; IL117963A0; CA2227428A1; EP0865315A2; MX9708060A; IL117963A; AU5551696A; JPH11503964A; KR19990007944A

Description

WO 96/33013 PCT/US96/05303 ENHANCED ADSORBENT AND ROOM TEMPERATURE CATALYST PARTICLE AND METHOD OF MAKING AND USING THEREFOR BACKGROUND OF THE INVENTION FIELD OF THE INVENTION This invention relates generally to adsorbent particles that have improved adsorbent properties and/or improved or newly existing catalytic properties, including room temperature catalyltic capability.

BACKGROUND ART Oxides of metals and certain non-metals are known to be useful for removing constituents from a gas or liquid stream by adsorbent mechanisms. For example, the use of activated alumina is considered to be an economical method for treating water for the removal of a variety of pollutants, gasses, and some liquids. Its highly porous structure allows for preferential adsorptive capacity for moisture and contaminants contained in gasses and some liquids. It is useful as a desiccant for gasses and vapors in the petroleum industry, and has also been used as a catalyst or catalystcarrier in air and in water purification. Removal of contaminants such as phosphates by activated alumina are known in the art. See, for example, Yee, "Selective Removal of Mixed Phosphates by Activated Alumina," JAmer. Waterworks Assoc., Vol. 58, pp.

239-247 (1966).

U.S. Patent No. 5,242,879 to Abe et al. discloses that activated carbon materials, which have been subjected to carbonization and activation treatments, and then further subjected to an acid treatment and a heat treatment in an atmosphere comprising an inert gas or a reducing gas, have a high catalytic activity and are suitable as catalysts for the decomposition of hydrogen peroxide, hydrazines or other water pollutants such as organic acids, quaternary ammonium-salts, and sulfur-containing SUBSTIUTE SHEET (RULE 26) WO 96/33013 PCTIUS96/05303 -2compounds. Acid is used to remove impurities and not to enhance the adsorbent features.

Ion implantation has been used in integrated circuit fabrication. U.S.

Patent No. 4,843,034 to Herndon et al. discloses methods and systems for fabricating interlayer conductive paths in integrated circuits by implanting ions into selected regions of normally insulative layers to change the composition and/or structure of the insulation in the selected regions. It is stated that a wide range of insulative materials can be rendered selectively conductive, including polymeric insulators and inorganic insulators, such as metal or semi-conductor oxides, nitrides or carbides. Insulators which can be processed according to this patent include silicone dioxide, silicon nitride, silicon carbide, aluminum oxides, and others. It is disclosed that implanted ions can include ions of silicon, germanium, carbon, boron, arsenic, phosphorous, titanium, molybdenum, aluminum, and gold. Typically, the implantation energy varies from about 10 to about 500 KeV. It is disclosed that the ion implantation step changes the composition and structure of the insulative layer and is believed also to have the effect of displacing oxygen, nitrogen, or carbon so as to promote the migration and alloying of metal from the conductive layer(s) into the implanted region during the sintering step. The implantation also is believed to have the physical effect of disrupting the crystal lattice, which may also facilitate the fusion of the metal. This results in a composite material in the implantation region essentially consisting of the disruptive insulator and implanted ions. In the working examples, ions of silicon were implanted into the particular region of the silicon dioxide layer using a direct implantation machine.

U.S. Patent No. 5,218,179 to Matossian et al. discloses a plasma source arrangement for providing ions for implantation into an object. A large scale object which is to be implanted with ions is enclosed in a container. The plasma is generated in a chamber which is separate from, and opens into the container for a plasma source ion implantation working volume. The plasma defuses from the chamber into the container to surround the object with substantially improved density compared to conventional SUBSTUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 -3practice. High voltage negative pulses are applied to the object, causing the ions to be accelerated from the plasma toward and be implanted into the object.

Thus, there has been a need in the art for adsorbents that have improved ability to adsorb particular materials, especially contaminants from a gas or liquid stream, to thereby purify the stream. Also, there has been a need in the art for catalysts that have the ability or that have an improved ability to catalyze the reaction of contaminants into non-contaminant by-products.

Additionally, there has been a need in the art for adequately agglomerating adsorbent particles together to form a composite particle for performing simultaneous multiple applications and purifications. In the prior art, particles have been ground up and extruded together to hold them in an agglomerated or combined state.

This has the drawback of requiring an expensive extrusion step, wherein particular equipment and processing time is needed to extrude the particles together.

None of the above-cited documents discloses compounds, compositions or processes such as those described and claimed herein.

SUMMARY OF THE INVENTION In accordance with the purpose(s) of this invention, as embodied and broadly described herein, this invention, in one aspect, relates to a method for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle, comprising the steps of: removing an effective amount of air from a closed chamber containing an adsorbent and/or catalytic particle, wherein the resultant chamber pressure is less than one atmosphere; raising the chamber pressure with an inert gas to at least one atmosphere; contacting the particle with an energy beam of sufficient energy for a sufficient time to thereby enhance the adsorbent and/or catalytic SUBS Un E SHET (RULE26) WO 96/33013 PCT/US96/05303 -4properties of the particle and/or produce catalytic properties in the particle.

The particle produced from this process can have room temperature catalytic capabilities towards particular contaminants.

The invention further provides a method for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle, comprising implanting oxygen into an adsorbent and/or catalytic particle.

In yet another aspect, the invention relates to the particle made by the process of the invention.

In yet another aspect, the invention relates to an enhanced adsorbent and/or enhanced catalytic particle and/or a catalytic particle comprising an adsorbent particle that has been treated to provide an excess of oxygen implanted at least on the surface of the particle to thereby form an enhanced adsorbent and/or enhanced catalytic particle and/or a catalytic particle.

20 In yet another aspect, the invention relates to a binder for binding adsorbent and/or catalytic particles to produce an agglomerated particle comprising colloidal aluminium oxide or colloidal silicon dioxide.and an acid.

o5 In yet another aspect, the inventiornrelates to a method for binding adsorbent and/or catalytic particles, comprising the steps of: mixing colloidal aluminium oxide or colloidal silicon dioxide with the particles and an acid; agitating the mixture to homogeneity; and heating the mixture for a sufficient time to cause cross- 30 linking of the aluminium oxide or colloidal silicon dioxide in the mixture.

SUBSTITUTE SHEET (RULE 26) SUBTITTESHEET (RULE 26) WO 96/33013 PCTIUS96/05303 In yet another aspect, the invention relates to a method for reducing or eliminating the amount of a contaminant from a liquid or gas stream comprising contacting the particle of the invention with the contaminant in the stream for a sufficient time to reduce or eliminate the amount of the contaminant from the stream.

In yet another aspect, the invention relates to a method for adsorbing a contaminant from a liquid or gas stream onto an adsorbent particle comprising contacting the particle of the invention with the contaminant in the stream for a sufficient time to adsorb the contaminant.

In yet another aspect, the invention relates to a method for catalyzing the degradation of a hydrocarbon comprising contacting the hydrocarbon with the particle of the invention for a sufficient time to catalyze the degradation of the hydrocarbon.

In yet another aspect, the invention relates to a method for reducing or eliminating the amount of a contaminant from a gas stream by catalysis comprising contacting the particle of the invention with a gas stream containing a contaminant comprising an oxide of nitrogen, an oxide of sulfur, carbon monoxide, or mixtures thereof for a sufficient time to reduce or eliminate the contaminant amount.

In yet another aspect, the invention relates to an apparatus for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle comprising: chamber means for containing the particle in a closed system having an inlet gas port, an exit gas port, and a target plate, said chamber means being capable of maintaining vacuum and positive pressures; means for providing an inert gas to the chamber means through the inlet gas port; means for withdrawing from the chamber means an effective amount of the ambient air therein so as to create a vacuum within the chamber means; and SUBSTUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 -6means for providing an energy beam to the chamber means, said energy beam means outlet being targeted at the target plate.

In yet another aspect, the invention relates to a method for increasing the surface area of an adsorbent and/or catalytic particle, comprising the steps of raising the chamber gauge pressure of a closed chamber containing the adsorbent and/or catalytic particle to at least 100 psi with an inert gas and rapidly decompressing the chamber pressure to thereby increase the surface area of the particle.

In yet another aspect, the invention relates to a method for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle, comprising the step of: contacting an adsorbent and/or catalytic particle with an energy beam of sufficient energy for a sufficient time to thereby enhance the adsorbent and/or catalytic properties of the particle and/or produce catalytic properties in the particle.

Additional advantages of the invention will be set forth in part in the description which follows, and in part will be obvious from the description, or may be learned by practice of the invention. The advantages of the invention will be realized and attained by means of the elements and combinations particularly pointed out in the appended claims. It is to be understood that both the foregoing general description and the following detailed description are exemplary and explanatory only and are not restrictive of the invention, as claimed.

The accompanying drawings, which are incorporated in and constitute a part of this specification, illustrate several embodiments of the invention and together with the description, serve to explain the principles of the invention.

SUBSTmIUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 -7- BRIEF DESCRIPTION OF THE DRAWINGS Fig. 1 shows an apparatus of one embodiment of the present invention for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle.

Fig. 2 is a graph showing the reduction of NO using a particle of the invention.

Fig. 3 is a graph showing the reduction of CO using a particle of the invention.

DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention may be understood more readily by reference to the following detailed description of preferred embodiments of the invention and the Examples included therein and to the Figures and their previous and following description.

Before the present compositions of matter and methods are disclosed and described, it is to be understood that this invention is not limited to specific synthetic methods or to particular formulations, as such may, of course, vary. It is also to be understood that the terminology used herein is for the purpose of describing particular embodiments only and is not intended to be limiting.

It must be noted that, as used in the specification and the appended claims, the singular forms "an" and "the" include plural referents unless the context clearly dictates otherwise.

In this specification and in the claims which follow, reference will be made to a number of terms which shall be defined to have the following meanings: SUBSTITTE ShEET (RULE 26) WO 96/33013 PCT/US96/05303 -8- "Optional" or "optionally" means that the subsequently described event or circumstance may or may not occur, and that the description includes instances where said event or circumstance occurs and instances where it does not.

The term "particle" as used herein is used interchangeably throughout to mean a particle in the singular sense or a combination of smaller particles that are grouped together into a larger particle, such as an agglomeration of particles.

The term "ppm" refers to parts per million and the term "ppb" refers to parts per billion. GPM is gallons per minute.

In accordance with the purpose(s) of this invention, as embodied and broadly described herein, this invention, in one aspect, relates to a method for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle, comprising the steps of: removing an effective amount of air from a closed chamber containing an adsorbent and/or catalytic particle, wherein the resultant chamber pressure is less than one atmosphere; raising the chamber pressure with an inert gas to at least one atmosphere; contacting the particle with an energy beam of sufficient energy for a sufficient time to thereby enhance the adsorbent and/or catalytic properties of the particle and/or produce catalytic properties in the particle.

SUBSTITUTE SHEEf (RULE 26) WO 96/33013 PCTIUS96/05303 -9- In yet another aspect, the invention relates to the particle made by the process of the invention.

In yet another aspect, the invention relates to a binder for binding adsorbent and/or catalytic particles to produce an agglomerated particle comprising colloidal aluminium oxide or colloidal silicon dioxide and an acid.

In yet another aspect, the invention relates to a method for binding adsorbent and/or catalytic particles, comprising the steps of: mixing colloidal aluminium oxide or colloidal silicon dioxide with the particles and an acid; agitating the mixture to homogeneity; and heating the mixture for a sufficient time to cause crosslinking of the aluminium oxide or colloidal silicon dioxide 20 in the mixture.

In yet another aspect, the invention relates to a method for reducing or eliminating the amount of a contaminant from a liquid or gas stream comprising contacting the particle of the invention with the contaminant in the stream for a sufficient time to reduce or eliminate the amount ofthe contaminant from the stream.

SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 10 In yet another aspect, the invention relates to a method for catalyzing the degradation of a hydrocarbon comprising contacting the hydrocarbon with the particle of the invention for a sufficient time to catalyze the degradation of the hydrocarbon.

In yet another aspect, the invention relates to an apparatus for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle comprising: chamber means for containing the particle in a closed system having an inlet gas port, an exit gas port, and a target plate, said chamber means being capable of maintaining vacuum and positive pressures; means for providing an inert gas to the chamber means through the inlet gas port; means for withdrawing from the chamber means an effective amount of the ambient air therein so as to create a vacuum within the chamber means; and means for providing an energy beam to the chamber means, said energy beam means outlet being targeted at the target plate.

SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 11 In yet another aspect, the invention relates to a method for producing an enhanced adsorbent and/or enhanced catalytic particle and/or for producing a catalytic particle, comprising the step of: contacting an adsorbent and/or catalytic particle with an energy beam of sufficient energy for a sufficient time to thereby enhance the adsorbent and/or catalytic properties of the particle and/or produce catalytic properties in the particle.

By enhanced adsorbent and/or enhanced catalytic particle, it is intended that the particles of this invention have improved adsorbent and/or improved catalytic properties over prior art adsorbent and/or catalytic particles. Also, by producing a catalytic particle, it is intended that some particles of the instant invention have catalytic properties for catalyzing the conversion of particular contaminants into other forms, whereas the same particles not treated by the process of the present invention possess no catalytic properties at least for those particular contaminants.

Enhanced adsorptive properties is intended to include both ion capture and ion exchange mechanisms. Ion capture refers to the ability of the particle to bond to other atoms due to the ionic nature of the particle. Ion exchange is well known in the art and refers to ions being interchanged from one substance to another. Adsorption is a term well known in the art and should be distinguished from absorption.

In the particle of this invention, typically any particle that initially has some adsorbent and/or catalytic properties can be used. For example, activated carbon and oxide particles can be oxygen implanted by the process of the present invention.

For oxide particles, oxides of metals or oxides of non-metals, such as silicon or germanium, are preferred. Even more preferred are oxides of transition metals, oxides of metals of Group III Al, Ga, In, TI) and IA (Li, Na, K, Rb, Cs, Fr) of the periodic table, and oxides of silicon. Particularly preferred oxides include aluminum oxide (A1 2 0 3 silicon dioxide (SiO2), manganese dioxide (MnO 2 copper SUBSTITTE SHEEF (RULE 26) WO 96/33013 PCTIUS96/05303 12oxide (CuO), iron oxide black (Fe30 4 iron oxide red (ferric oxide or Fe 2 0 3 zinc oxide (ZnO), zirconium oxide (ZrO 2 vanadium pentoxide (V 2 0 5 and titanium dioxide (Ti02).

In one embodiment, the particle comprises alumina oxide that has been pre-treated by a full calcination process. Calcined aluminum oxide particles are well known in the art. They are particles that have been heated to a particular temperature to form a particular crystalline structure. Processes for making calcined aluminum oxide particles are well known in the art as disclosed in, Physical and Chemical Aspects of Adsorbents and Catalysts, ed. Linsen et al., Academic Press (1970), which is incorporated by reference herein. In one embodiment, the Bayer process can be used to make aluminum oxide precursors. Also, pre-calcined aluminum oxide, that is, the aluminum oxide precursor (A(OH) 3 and calcined aluminum oxide are readily commercially available. Calcined aluminum oxide can be used in this dried, activated form or can be used in a partially or near fully deactivated form by allowing water to be adsorbed onto the surface of the particle. However, it is preferable to minimize the deactivation to maximize the adsorbent capability.

In a preferred embodiment, the aluminum oxide has been produced by calcining at a particle temperature of from 400 0 C to 700*C. These preferred aluminum oxide particles are preferably in the gamma, chi-rho, or eta forms and have a pore size of from 3.5 nm to 35 nm diameter and a BET surface area of from 120 to 350 m2/g.

For activated carbon, any of the activated carbons useful in the adsorbent art can be used. Preferably coal based carbon or coconut based carbon are used.

Generally, coal based carbon can be used to remediate aqueous contaminants while coconut based carbon can be used to remediate airborne or gaseous contaminants.

Preferably, the activated carbon is less than 20 microns in size for ease of mixing and extrusion.

SUBSITUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 13 The particle of the invention can be used alone, in combination with identical or different type composition particles prepared by the processes of the invention, and/or in combination with other adsorbent or catalytic particles known in the art. The particles can be combined in a physical mixture or agglomerated using techniques known in the art or disclosed herein. In a preferred embodiment, different composition type particles are combined by agglomeration to form a multifunctional composite particle. In this embodiment, particles can be used to achieve multiple functions simultaneously, such as by removing multiple contaminants, by taking advantage of the individual effects from each of the types of particles. Co-particles that are preferably used in this invention include all particles previously disclosed and zeolite.

In one embodiment, the composite particle comprises aluminum oxide and a second particle of titanium dioxide, copper oxide, vanadium pentoxide, silicon dioxide, manganese dioxide, iron oxide, zinc oxide, activated carbon, or zeolite. In another embodiment, the composite particle comprises aluminum oxide and activated carbon. In another embodiment, the particle comprises activated carbon (coal-based), activated carbon (coconut-based), silicon dioxide, and aluminum oxide. In a preferred embodiment, this particle is used to remediate aqueous contamination. In one embodiment, this particle of coal-based activated carbon, coconut-based activated carbon, silicon dioxide, and aluminum oxide is used to remediate aqueous contaminants, such as 1,2-dibromo-3-chloropropane (DBCP), radon, and heavy metals, from a contaminated water source.

The particles of this invention can be subjected to other surface treatments prior to or after being treated by the process of the present invention. The particles of the invention can be pretreated by processes known in the art to improve their adsorptive capability, such as by calcination. Calcination refers to heating a solid to a temperature below its melting point to alter the crystal structure to a particular form. The calcinated particle can be dried or maintained in dry form creating an activated particle or, if water is absorbed on the particle, the particle can be partially or S IBS1uTE SVEET (RULE 26) WO 96/33013 PCTIUS96/05303 -14near fully deactivated. In one embodiment, the particles of this invention can be in dry, slurry, or gel form. The particle size can vary depending on the end use, ranging in sizes known in the art, such as colloidal, microscopic, or macroscopic. Preferably, the particles prior to agglomeration are less than 20 microns in size for ease of mixing and extrusion.

Binders for binding the individual particles to form an agglomerated particle are known in the art or are described herein. In a preferred embodiment, the binder can also act as an adsorbent and/or a catalyst. A preferred binder for the agglomerated particle is colloidal alumina or colloidal silica. At approximately 450 °C, the colloidal alumina goes through a transformation stage and cross-links with itself.

Lower temperatures will also cross-link the colloidal alumina.

Colloidal silica cross-links with itself if it is sufficiently dried to remove water. Preferably, from about 20 wt. to about 99% of the total mixture is colloidal alumina or colloidal silica to provide the necessary crosslinking during heating to bind the agglomerated particle into a water-resistant particle. The particle can then withstand exposure to all types of water for an extended time and not degrade.

In one embodiment, the agglomerated particle is made by mixing colloidal alumina with the adsorbent particles. Typically, from about 20% to about 99% 20 by weight of the mixture is colloidal alumina. The particle mixture is then mixed with an acid solution such as, for example, nitric, sulfuric, hydrochloric, boric, acetic, formic, phosphoric, and mixtures thereof In one embodiment the acid is 5% nitric acid solution. The colloidal alumina, adsorbent particles, and acid solution are thoroughly mixed so as to create a homogenous blend of all elements. Then additional acid solution 25 is added and further mixing is performed until the mixture reaches a suitable consistency for agglomeration. After agglomeration is complete, the agglomerated particles are heated to at least 450 0 C to cause the colloidal alumina crosslinking to occur.

.9 Sources and/or methods of making the starting materials for the various adsorbent particles of the present invention are readily available and are well-known to those of ordinary skill in the art.

1r 'SUBSTITUTE SHEET (RULE 26) I LIIi

I

WO 96/33013 PCTIUS96/05303 For an explanation of the process used to make a particle of one embodiment of this invention, reference is made to Figure 1. The apparatus of this embodiment is designated generally as 10. The particulate material or target media to be treated is placed in a chamber 11 on ungrounded target plate 22. In one embodiment, the target plate can be rotated to provide more efficient treatment of the particle by the energy beam. Chamber 11 is preferably made of a dielectric material.

Chamber 11 is sealed by a compression plate latched door 12 that has the ability to withstand high compression ratios both in the positive as well as negative pressures.

Pressure is monitored with pressure gauge 18. Vacuum conditions are created in the chamber using vacuum pump 19 to evacuate an effective amount of air initially contained in the chamber. Air can be detrimental to the oxygen implantation step in that it reduces the efficiency of the energy beam's affect on the particle. Evacuating an effective amount of air is intended to mean that enough air is removed so that the energy beam has the ability to enhance the adsorbent and/or catalytic properties and/or produce catalytic properties in the particle. Typically, vacuum pump 19 is used to evacuate as much air as possible from chamber 11 to maximize the energy beam's efficiency and to allow a beam of lower energy to be used. The chamber is brought up to a pressure of at least atmospheric pressure using an inert gas from cylinder 13 through a high pressure injector 17. In one embodiment, the gauge pressure (pressure above atmospheric) is from 1 to 5,000 psi. Typically, the gauge pressure can be at least about 20 psi to prevent arcing.

The inert gas is typically any gas that is inert to chemically reacting with and degrading the adsorbent particle, and yet, does not impede the energy beam's effectiveness in implanting the oxygen. Typical inert gases include the noble gases, such as helium, neon, argon, krypton, xenon, and radon.

The energy source is targeted at the particle contained in the chamber through an energy injector 15 located at the end of the energy source 14. The energy source can be of any high energy that can force oxygen into the particle and/or add excess charge to the particle. Typically, the energy source is an ion machine which SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCTIUS96/05303 -16concentrates an ion or electron beam, such as a broad beam ion source or a wide beam photoionizer. In a specific embodiment, the energy source can be a broad beam ion source, manufactured by Commonwealth, Alexandria, Virginia, U.S.A. having a maximum output of 25 eV. The energy source 14, utilizes a power supply 21. In a specific embodiment, the power supply can be a Commonwealth IBS-250 high voltage power supply rated up to 1500V with remote operation capabilities. Additionally, the energy beam causes the inert gas to become ionized. The charge introduced into the chamber is at a level sufficient to enhance the adsorbent and/or catalytic properties of the particle and/or produce catalytic properties in the particle. In one embodiment, an electron beam of 15 to 20 eV was used, although a smaller or larger amount of energy can be used. Once the proper charge has been attained for a sufficient time, the energy source is turned off. This sufficient time can be very short, on the order of less than a second to about 10 seconds, although a longer time is not detrimental. Then, the chamber pressure is decompressed via a release valve 16.

Not wishing to be bound by theory, it is theorized that the energy beam causes monoatomic oxygen present on the surface of the particle to be pushed below the surface of the particle, which then becomes tightly bound to the internal structure of the particle. For crystalline particles, the oxygen becomes tightly bound within the crystal lattice. The monoatomic oxygen originates from oxygen that is on the outer surface of the crystal lattice of the particle or from residual water or air on the surface of the particle. This increases the adsorbent and/or catalytic characteristics of the particle and can create catalytic properties, including room temperature catalytic capabilities, in the particle. It is additionally theorized that the advantageous properties of the particle of this invention result from the energy beam adding an electrical charge or increased electrical charge to the particle.

In another embodiment, in the energy beam proces above, after the air has been removed from the chamber, inert gas is added so that the chamber pressure is brought up to a high pressure. Typically, the gauge pressure can be from about at least 100 psi, more preferably at least 1,000 psi, even more preferably at least 5,000 psi.

SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCTIUS96/05303 -17- Even higher pressures can be used if the chamber 15 of a high enough pressure rating.

The high pressure or compression is maintained for a sufficient time to increase the density of the particle. Residual air is bled from the vessel, thereby removing any residual air from a puffed up particle, until a constant pressure can be maintained.

Typically, about ten minutes of high pressure is sufficient. After the energy source has been introduced for a sufficient time in the chamber as described above, the energy source is turned off and then the chamber pressure is rapidly decompressed via release valve 16. By rapidly, it is preferably meant about 3 seconds. This increases the surface area of the particle.

Not wishing to be bound by theory, it is theorized that as the pressure from the chamber is rapidly released, the contents of the chamber expand simultaneously but at different rates of expansion. The charged inert gas expands at a much faster rate than that of the particulate matter due to the density differences between the two substances. Due to this expansion rate difference, the charged inert gas travels rapidly and penetrates or explodes into and through the particles. This rapid penetration alters the pore structure and increases the amount of pores of the particle. The surface area of the particle is thereby greatly increased, increasing the overall adsorption capability of the particle. Depending on the particle employed, the BET surface area can be increased at least more preferably at least even more preferably at least 10%, even more preferably at least 20%, even more preferably at least 30%. The lower density particles, such as activated carbon, can achieve a greater increase in surface area.

The chamber pressure and the energy level can be varied to produce different effects to meet the particular physical and chemical requirements for the specific particle end use. Varying the pressure and energy level parameters can alter the ability of the particle to adsorb a particular contaminant.

In another embodiment of this invention, the surface area enhancement aspect of the process can be practiced alone without the energy beam aspect. In this embodiment, the inert gas only needs to be inert to the particle and does not have to be SUBSTUTE SHEEl (RULE 26) WO 96/33013 PCT/US96/05303 18inert to the effects of the energy beam. Thus, gases such as air and CO 2 can also be used in the this embodiment.

In another embodiment, the energy beam aspect can be practiced alone without the surface area enhancement aspect. In this embodiment, the energy beam is targeted directly at the particle to implant oxygen within the particle. This can be done in the batch process described above or a semi-batch or continuous process. In a semibatch process, particles are automatically moved into the chamber where they are treated and automatically removed from the chamber. In a continuous process, in one embodiment, the particles are provided on a conveyor belt system. Air is displaced from the area around the particles by inert gas to provide a viable path for the energy beam, which is set up along side or overhead of the conveyer belt system. The energy beam is either continuously on or is turned on as the particles reach a specific point along the conveyer belt system. In a variation of the embodiments of this invention, the air removal and replacement with inert gas steps in the batch or semi-batch processes and the air displacement by inert gas step in the continuous process can be avoided by using an extremely high level of energy source, such that, the air does not impede the oxygen from penetrating the surface of the particle. In another embodiment of a continuous process, the particles are filtered through a mesh screen sieve, which has been substantially ionized to cause the oxygen on the particle to penetrate the particle.

The particles of this invention are characterized by having an increased level of oxygen at least on the surface of the particle. This increased level of oxygen is higher than the total of the stoichiometric amount of oxygen expected in the particle and that found as residual oxygen on the surface of the particle. The oxygen implanted particle has at least 1.1 times the oxygen atom per cent to non-oxygen atom per cent ratio at its surface compared to the initial non-oxygen implanted particle, wherein the surface characterization is determined by an x-ray photoelectron spectroscopy (XPS or ESCA) spectrometer, a device well known to those of skill in the art. Even more preferably, the particle has at least a 1.5 fold increase in oxygen ratio, even more preferably the particle has at least a 2 fold increase in oxygen ratio, even more SUBSTITUT SHEE (RULE 26) WO 96/33013 PCT/US96/05303 -19preferably, at least a 4 fold increase in oxygen ratio, even more preferably at least a 6 fold increase in oxygen ratio.

The particle of this invention can be used in any adsorption and/or catalytic application known to those of ordinary skill in the art to achieve superior results over prior art particles. Additionally, the particle of the invention can be used in various adsorption and/or catalytic applications never before contemplated in the art. In one embodiment, the particle is used for environmental remediation applications. In this embodiment, the particle can be used to remove contaminants, such as heavy metals, organics, including for example but not limited to, chlorinated organics and volatile organics, inorganics, or mixtures thereof. Specific examples of contaminants include, but are not limited to, acetone, microbials, ammonia, benzene, carbon monoxide, chlorine, dioxane, ethanol, ethylene, formaldehyde, hydrogen cyanide, hydrogen sulfide, methanol, methyl ethyl ketone, methylene chloride, nitrogen oxides, propylene, styrene, sulfur dioxide, toluene, vinyl chloride, arsenic, lead, iron, phosphates, selenium, cadmium, uranium, plutonium, radon, 1,2-dibromo-3-chloropropane (DBCP), chromium, tobacco smoke, and cooking fumes. The particle of this invention can remediate individual contaminants or multiple contaminants from a single source.

For environmental remediation applications, typically, particles of the invention are placed in a container, such as a filtration unit. The contaminated stream enters the container at one end, contacts the particles within the container, and the purified stream exits through another end of the container. The flow rate of the contaminant stream and the amount of particle material needed can be determined by one of skill in the art with routine experimentation by determining the capacity needed.

The particles contact the contaminants within the stream and bond to and remove the contamination from the stream. The particles can also eliminate certain contaminants by catalyzing the conversion of the contaminants into other components. Typically, in the adsorption application, the particles become saturated with contaminants over a period of time, and the particles must be removed from the container and replaced with fresh particles. The contaminant stream can be a gas, such as air, or liquid, such as water.

SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 In the adsorption application, the particle of this invention bonds with the contaminant so that the particle and contaminant are tightly bound. This bonding makes it difficult to remove the contaminant from the particle, allowing the waste product to either be disposed of into any public landfill or used as a raw material in the building block manufacturing industry. Measurements of contaminants adsorbed on the particles of this invention using a Toxic Chemical Leachate Permit (TCLP) test known to those of skill in the art showed that there was a bond at least as strong as a covalent bond between the particles of this invention and the contaminants.

The particles of this invention have superior ability to adsorb contaminants due to enhanced physical and chemical properties of the particle. The particles of this invention can adsorb a larger amount of adsorbate per unit volume or weight of adsorbent particles than a non-enhanced particle. The particle of this invention surprisingly removes contaminants in various streams at both high and low concentrations of contaminants. Also, the particles of this invention can reduce the concentration of contaminants or adsorbate material in a stream to a lower absolute value than is possible with a non-enhanced particle. In particular embodiments, the particles of this invention can reduce the contaminant concentration in a stream to below detectable levels, never before achievable with prior art particles.

The particles of this invention can also have a newly added catalytic property. Specifically, the increased oxygen content in the particle matrix allows the particle to act as a catalyst. For example, the particle has the ability to catalyze the break down of hydrocarbon compounds and has the ability to catalyze the conversion of CO, SO x or NO x into other components, even at low heat or room temperatures.

Particular end uses contemplated by this invention include, but are not limited to, reducing or eliminating contaminants for particular applications, such as waste water treatment facilities, sewage facilities, municipal water purification facilities, in-home water purification systems, smoke stack effluents, vehicle exhaust effluents, engine or motor effluents, home or building air purification systems, home radon SUBSTIUTE SHET (RULE 26) WO 96/33013 PCT/US96/05303 -21remediations, landfill leachates, manufacturing facility chemical waste effluents, and the like.

Prior art adsorbents, such as activated carbon, when sprayed with antimicrobials, tend to lose their adsorbent properties. Conversely, the increased adsorbent properties allow the particles of the present invention to be sprayed with anti-microbials while still retaining the particle's adsorbent properties. Moreover, unlike prior art particles, contact with water does not deactivate the adsorption capability of the inventive particles.

Experimental The following examples are put forth so as to provide those of ordinary skill in the art with a complete disclosure and description of how the compounds claimed herein are made and evaluated, and are intended to be purely exemplary of the invention and are not intended to limit the scope of what the inventors regard as their invention.

Efforts have been made to ensure accuracy with respect to numbers amounts, temperature, etc.) but some errors and deviations should be accounted for. Unless indicated otherwise, parts are parts by weight, temperature is in *C or is at or near room temperature and pressure is at or near atmospheric.

Example 1.

Various particles were made in accordance with the procedures of this invention as follows. The procedures used to prepare the particle designated as 1 a in Table 1 below, having a composition of 60% A1 2 0 3 20% carbon, 15% manganese dioxide and 5% copper oxide, is exemplified. The alumina utilized was a gamma calcined (550*C) alumina derived from a high density, low porosity pseudoboehmite alumina or alumina gel. The alumina was pretreated by calcining to 550" C to reach the desired gamma crystalline structure. The carbon utilized in this particle was a coconut based carbon, designated as Polynesian coconut based carbon purchased from Calgon SUBSTTUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 22 Carbon Corporation. Due to the use of coconut shells in the manufacture of this carbon, there exists a very large surface area as well as micro-pores which are useful for removing contaminants in a gas stream. The four individual particle types were mixed together in their appropriate weight per cents according to the dry weight. They were mixed together into a homogenous dry mixture. An acid solution of 20 parts by weight of 80% nitric acid was added to 80 parts by weight of water. The acid solution was added to the dry particle mixture slowly until the mixture obtained a moist pasty consistency. This consistency allowed the mixture to be extruded into the desired form.

The mixture was extruded using a LCI model BTG® laboratory extruder. After the mixture was extruded, the extrudate was chopped up into approximately one-sixteenth to one-eighth inch particles and then was dried at a temperature of at least 450° C to cross-link the aluminum oxide. The particles were placed in a vacuum/pressure vessel chamber on an ungrounded target plate. The door to the chamber was secured, and air was pumped out of the chamber down to a negative pressure of two militorrs. Upon reaching this pressure, argon gas was allowed to bleed into the chamber and reach an internal gauge pressure of about 20 psi. Upon reaching this pressure, the energy beam source was activated to 15 to 20 eV and was applied to the particle on the target area.

A Commonwealth broad beam ion source was used. Treatment times for the particles vary according to the amount and density of material on the target. For this example, a volume of 50 grams of material was used and a treatment time often seconds was used.

The treatment times also vary according to the output power from the energy beam source and the internal pressure in the chamber. After ten seconds, the ion source was turned off and the chamber was evacuated to atmospheric pressure. The sample was then removed from the chamber.

Particles lb through lac were similarly made in accordance with the abovedescribed example for 1 a except that the particular compositions were as set forth in Table 1. Also, the carbon utilized for aqueous particle designations lv and lw was a coal based carbon. This coal based carbon was purchased from Calgon Carbon Corporation as WHP grade carbon. The particular alumina utilized in particles lb through 1 ac was the same as described above for particle 1 a, a gamma calcined alumina.

SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCTIUS96/05303 -23 The other components listed below in Table 1 are well known and are readily available to one of skill in the art.

Each of the particle's composition made in accordance with the procedures of this invention described above and the contaminant it was tested with in Examples 2 and 3 are listed below in Table 1. The same particle designation system is used in Tables 1-3.

SUBSiE SHEEF (RULE 26) WO 96/33013 WO 9633013PCTIUS96/05303 24 TABLE 1 PARTICLE COMPOSITON' CONTAMINANTS DESIGNATION (weight ARON

QEU

18a 60% A1 2 0 3 20% Carbon, 15% Acetone 1 b2' 5% lb 100% A.1 2 0 3 Ammonia Ic 50% A1 2 0 3 40% Carbon, 10% Benzene S'0 2 Id 40% A1 2 0 3 30% V 2 05, 20% Carbon Monoxide MnO 2 10% TiO 2 le 100% A1 2 0 3 Chlorine if 100 A1 2 0 3 1 ,4-Dioxane Ig 100% A1 2 0 3 Ethanol lh 100% A1 2 0 3 Formaldehyde Ii 40% A1 2 0 3 30% MWO 2 200% Hydrogen Cyanide

V

2 05, 5% Zeolite, 5% FC 2

O

3 lj 30% A1 2 0 3 50% MnO 2 5% Hydrogen Sulfide Carbon, 5% Si0 2 10% ZnO 1k 90% A1 2 0 3 10% Carbon Methanol 11 100% A1 2 0 3 Methyl Ethyl Ketone I m 40% A1 2 0 3 20% MnO 2 10% Methylene Chloride 30% V 2 0 5 In 40% A1 2 0 3 30% V 2 0 5 20% Nitrogen Oxides 2 10% TiO 2 lo 30% A1 2 0 3 70% Carbon Propylene lp 30% Ai 2 0 3 70% Carbon Styrene I q 100% A1 2 0 3 Sulfur Dioxide I r 40% A1 2 0 3 30% MnO 2 30% Toluene Carbon Is 30% A1 2 0 3 70% Carbon Vinyl Chloride it 100% A1 2 0 3 Arsenic iu 100% A1 2 0 3 Cadmium IV 40% A1 2 0 3 40% Carbon, 20% Chlorine 50 2 I SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 TABLE 1 PARTICLE COMPOSITION' CONTAMINANTS DESIGNATION (weight AIRBORNE AQUEOUS 1w 40% A1 2 0 3 40% Carbon, 20% DBCP SiO 2 Ix 100% A1 2 0 3 Iron ly 100% A1 2 0 3 Lead 1z 100% A1 2 0 3 Phosphate 1 aa 40% A1 2 0 3 40% Carbon, 20% Radon SiO 2 lab 100% Al 2 0 3 Selenium l ac 100% A 2 0 3 Uranium Activated carbon coconut based was used for the airborne contaminants and for 1 aa (radon) and activated carbon coal based was used for aqueous contaminants lv and lw.

Example 2.

The particles made in Example 1 were tested for their ability for removal of various components from air. The tests for the airborne contaminants as summarized in Table 2 below were performed as follows. The contaminant source used was either solvent vapor or an off the shelf bottled gas mixture. Solvent vapor was mixed with humid air by injecting into the system with a syringe pump. A gas bottle with a needle valve and a flow meter, either a rotameter or a mass flow meter controller, was used to blend the gas bottle effluent with the humid air. Humid air at 30% relative humidity and °C was mixed with either the solvent vapor or gas stream. The humid air was generated by a flow-temperature-humidity control module which controlled temperature, relative humidity and the flow rate of the humid air. The concentration of the airborne contaminant in the humid air was then measured by an infrared analyzer.

After the influent infrared analysis, the sample entered a sample holder. The sample holder was a three-inch diameter test vessel, which held a 200 gm amount of particle sample in place using a fritted disk. After passing through the particles, the concentration of the contaminant in the effluent exited the sample holder. The SUBSTITUTE SHEET (RULE 26) WO 96/33013 PTU9/50 PCT[US96/05303 -26 concentration of the contarinent in the effluent side of the particle sample holder was also analyzed with an infrared analyzer. The test time was ten minutes. Percent removal was calculated as (initial contaminant concentration minus effluent contaminant concentration) divided by initial contaminant concentration.

The results are set forth in Table 2 below.

TABLE 2

INITAL

PARTICLE AIRBORNE CONTAMINANT PERCENT FLOW DESIGNATION CONTAMINANT CONCENTRATION REMOVAL RATE" I a Acetone 750 100 lb Ammonia 50 100 40 ft/min.

Ic Benzene 50 100 40 ftmin.

I d Carbon Monoxide 10000 100 40 ft/min.

Ie Chlorine 34 100 40 ft/min.

if 1 ,4-Dioxane 50 100 40 ft/mmi.

I g Ethanol 1000 100 40 ft/min.

lh Formaldehyde 10 100 40 ft/min.

I i Hydrogen Cyanide 20 100 40 ft/nun.

Ij Hydrogen Sulfide 20 100 40 ft/min.

1k Methanol 200 100 40 ft/min.

I1 Methyl Ethyl 1000 100 40 ftlmin.

Ketone Im Methylene chloride 50 100 40 ft/mix'.

In Nitrogen Oxides 100 100 40 ft/min.

Propylene 700 100 40 ft/mmi.

lp Styrene 50 100 40 ftfmin.

Iq Sulfur Dioxide 20 100 40 ft/min.

Ir Toluene 100 100 40 ft/min.

Is Vinyl Chloride 20 100 40 ft/mix'.

ft/mmn velocity was 55.5 I/min volumetric flow.

SUBSITT SHEEF (RULE 426) WO 96/33013 PCT/US96/05303 -27 In Table 2 above, for the formaldehyde test using particle Ih, formaldehyde was not detected on the particle after the test was completed and, as shown in Table 2, no formaldehyde was detected in the effluent stream. This particle lh acts as a catalyst towards formaldehyde and breaks down the formaldehyde into what is believed to be CO 2 and water, even at room temperature. This was further evidenced by a separate test in which it was shown that the formaldehyde was removed from the system over a substantially longer period of time than can be explained if the particle acted only as an adsorbent.

As can also be seen from the above Table 2, carbon monoxide and nitrogen oxides were not detected in the effluent system. Because these two components do not normally adsorb to the particle of the type used in this test, these particles act as a catalyst towards CO and NO x It is believed that the CO is converted to CO 2 and water and the NO x are converted to N 2 and 02. It is also believed that the remediation of SO 2 was through, at least in part, a catalysis reaction that converted SO 2 into other components. The catalyzed reactions were surprisingly achieved even at room temperature.

Example 3.

The particles made in Example 1 were tested for their ability for the removal of various components from water. The test procedures were as follows. For each contaminant run, 5 glass columns of 0.875 inch inner diameter by 12 inches long were prepared, each having a bed volume of test particle of 95 mls. Each bed was flushed with five bed volumes of deionized water by downward pumping at 6 gpm/ft 2 of cross-sectional flow rate about 95 ml/min). Each of the flow rates listed in Table 3 is per foot squared of cross-sectional flow rate. Test solutions for each of the aqueous contaminants were prepared. A total often bed volumes, that is, about one liter per column of aqueous contaminant test solution, was pumped through each of the columns.

During each run, the aqueous contaminant test solutions were continuously stirred at low speed prior to entry into the glass column to maintain a homogenous composition.

SUBSTITUTE SHEET (RULE 2) WO 96/33013 PCT/US96/05303 28 During the tenth bed volume, an effluent sample from each column was collected and analyzed for the particular aqueous contaminant. Additionally, a single influent sample for each test was collected and analyzed for the contaminant concentration.

The results of these tests are set forth in Table 3 below.

TABLE 3 PARTICLE AQUEOUS DESIG- CON- INFLUENT EFFLUENT FLOW DETECTION NATION TAMINANT RATE LIMIT It Arsenic 2,890 ppb 10ppb 5-6 GPM lu Cadmium 1,003 ppb <10 ppb 5-6 GPM 10 ppb Iv Chlorine 263 ppb <10 ppb 5-6 GPM 10 ppb lw DBCP (sw) 230.0 <0.02 Ag/1 5-6 GPM 0.02 /g/l 1,2-Dibromo- ug/l <0.02 ug/l 5-6 GPM 0.02 ,g/l 3- (sw) 210.0 <0.02 ug/1 5-6 GPM 0.02 tug/1 Chloropropane ug/1 (gw) 0.07 '"gh lx Iron 1.15 mg/i <0.03 mg/1 5-6 GPM 0.03 pg/l ly Lead 215 ppb 10ppb 5-6 GPM lz Phosphates 40.45 mg/l 9.50 mg/i 5-6 GPM N/A laa Radon 1,104.2 303.2 pCi/I 5-6 GPM N/A pCi/l 306.1 pCi/l 5-6 GPM 911.6 pCi/I lab Selenium 1.45 mg/i 0.003 mg/i 5-6 GPM 0.003 mg/1 lac Uranium 50.5 ppm 0.08 ppm 5-6 GPM N/A Synthetic water ground water Example 4.

A particle of 100% activated carbon coconut based of the present invention was prepared in accordance with the procedures of Example 1 above. An ESCA spectrometer was used to analyze the surface composition for the original SUBSTITUE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 -29 activated carbon particle and the particle after it was prepared using the process of Example 1. The surface characterization results are as follows.

TABLE 4 ACTIVATED CARBON INITIAL ACTIVATED PARTICLE OF THIS ELEMENT CARBON PARTICLE INVENTION (Atom (Atom Carbon 96.47 61.65 Oxygen 3.53 16.37 Sodium 0.59 Fluorine 8.61 Potassium 7.60 Chlorine 1.61 Sulfur 0.86 Phosphorus 0.55 Magnesium Thus, the initial particle had an oxygen/carbon ratio of about 0.04, whereas the treated activated carbon particle of this invention had an oxygen/carbon ratio of about 0.27, for an increased oxygen/carbon ratio of about 7 times the original ratio. A similar test was run on 100% aluminum oxide prepared according to the process of Example 1. The oxygen/aluminum ratio was increased at least about 2 fold over the original untreated particle oxygen/aluminum ratio.

Example A TCLP test was run on two different contaminant remediation applications of this invention. The particles were prepared by the procedures of Example 1 and were used to adsorb the particular contaminants in Table 5 below. In accordance with the EPA test methods, the particles were, inter alia, washed with an SUBSTITUTE SHEET (RULE 26) WO 96/33013 PCT/US96/05303 acid solution and tumbled for the requisite length of time. The concentration of the contaminants removed from the particle were then measured. The results are set forth below in Table TABLE EPA TCLP TCLP PARTICLE CONTAMINANT TEST CONTAMINANT PQL' METHOD (mg/1) 100% A1 2 0 3 Lead 1311/6010 0.50 0.50 100% A1 2 0 3 Phosphate 1311/365.4 <0.12 0.1 1 PQL is the practical quantitation limit, which is an EPA standard, and is different than the lowest detectable limit.

2 TCLP measures for phosphorus.

Thus, the particles of the invention, when acting as an adsorbent, bond tightly to the contaminants.

Example 6.

A fixed bed reactor was charged with 158 g, 9.4 cubic inches (2 inches diameter x 3 inches high) of the particles of Example 1(d) (40% A1 2 0 3 30% V205, MnO 2 10% TiO 2 A mixture of 101.8 ppm NO and 1,035 ppm CO in air was fed into the fixed bed reactor at room temperature at a rate of 35 standard cubic feet per hour (SCFH). The effluent of the fixed bed reactor was fed into a Horiba CLA-510SS NO x analyzer and a VIA-510 CO analyzer. The NO concentration dropped immediately reaching 5.4 ppm by 5 minutes (the first recorded measurement) and continued to drop to 4.0 ppm by 40 min. (See, Figure The CO concentration dropped more slowly, dropping to 532 ppm at 40 min. (See, Figure The test was stopped shortly after minutes. The CO concentration was still decreasing at 40 min. and may decrease further SUBSTITUTE SHEET (RULE 26) pCTUS96/05303 WO 96/33013 -31 upon further reaction time. It is believed that the particles of the invention catalytically degrade the CO and NO.

Throughout this application, various publications are referenced. The disclosures of these publications in their entireties are hereby incorporated by reference into this application in order to more fully describe the state of the art to which this invention pertains.

It will be apparent to those skilled in the art that various modifications and variations can be made in the present invention without departing from the scope or spirit of the invention. Other embodiments of the invention will be apparent to those skilled in the art from consideration of the specification and practice of the invention disclosed herein. It is intended that the specification and examples be considered as exemplary only, with a true scope and spirit of the invention being indicated by the following claims.

For the purposes of this specification it will be clearly understood that the word "comprising" means "including but not limited and the word "comprises" has a corresponding meaning.

The term "consistng essentially of" means that unavoidable impurities may be present, provided that no material change in properties results from their presence.

Claims

1. A binder for binding adsorbent and/or catalytic particles to produce an agglomerated particle including colloidal aluminum oxide or colloidal silicon dioxide and an acid.

2. The binder of Claim 1, wherein the acid is nitric acid.

3. A method for binding adsorbent and/or catalytic particles, including the steps of: mixing colloidal aluminum oxide or colloidal silicon dioxide with the particles and an acid; agitating the mixture to homogeneity; and heating the mixture for a sufficient time to cause cross-linking of the aluminum oxide or colloidal silicon dioxide in the mixture.

4. The method of Claim 3, wherein the colloidal aluminum oxide or colloidal silicon dioxide is from 20% to 99% by weight of the mixture. l S*

5. The method of Claim 3, wherein the acid is nitric acid.

6. The binder of Claim 1, wherein the binder includes colloidal aluminum oxide and an acid.

7. The binder of Claim 1, wherein the binder includes colloidal silicon dioxide and an acid.

8. A binder for binding adsorbent and/or catalytic particles to produce an agglomerated particle consisting essentially of colloidal aluminum oxide or colloidal silicon dioxide and an acid.

9. The method of Claim 3, wherein in the mixing step, colloidal aluminum oxide is mixed with the particles and the acid.

The method of Claim 3, wherein in the mixing step, colloidal silicon dioxide is mixed with the particles and the acid. 33

11. The method of Claim 3, wherein the acid includes nitric acid, sulfuric acid, hydrochloric acid,-acetic acid, formic acid, phosphoric acid, or a mixture thereof.

12. The method of Claim 3, wherein the acid is a 5% nitric acid.

13. The method of Claim 3, wherein in the mixing step, 20 to 99% by weight colloidal aluminum oxide is mixed with 5% nitric acid.

14. An adsorbent and/or catalytic particle system, including a first particle ofan adsorbent and/or catalytic particle and a binder including colloidal aluminum oxide or colloidal silicon dioxide, wherein the binder is cross-linked.

15. The particle system of Claim 14, wherein the binder includes colloidal aluminum oxide.

16. The particle system of Claim 14, wherein the binder includes colloidal silicon dioxide. S

17. The particle system of Claim 14, wherein the binder is cross-linked with itself. S:

18. The particle system of Claim 14, wherein the binder is cross-linked with the first particle.

19. The particle system of Claim 14, wherein the binder is cross-linked with itself and the •first particle.

The particle system of Claim 14, wherein the first particle includes an oxide particle or activated carbon.

21. The particle system of Claim 14, wherein the first particle includes an oxide of metal, an oxide of silicon or activated carbon.

22. The particle system of Claim 14, wherein the first particle includes aluminum oxide, titanium dioxide, copper oxide, vanadium pentoxide, silicon dioxide, manganese dioxide, A505 iron oxide, zinc oxide, activated carbon, or zeolite.

23. The particle system of Claim 14, wherein the first particle includes aluminum oxide.

24. The particle system of Claim 23, further including a second particle of titanium dioxide, copper oxide, vanadium pentoxide, silicon dioxide, manganese dioxide, iron oxide, zinc oxide, activated carbon, or zeolite.

The particle system of Claim 14, wherein the first particle includes aluminum oxide and activated carbon.

26. The particle system of Claim 25, wherein the first particle further includes silicon dioxide and wherein the activated carbon is a mixture of coal based and coconut based activated carbon.

27. The particle system of Claim 14, wherein the binder is from 20 to 99% by weight of the particle.

28. A method for reducing or eliminating the amount of a contaminant from a liquid or gas •stream including contacting an adsorbent and/or catalytic particle system including (a) a first particle of an adsorbent and/or catalytic particle and a binder including colloidal aluminum oxide or colloidal silicon dioxide, wherein the binder is cross-linked, with the contaminant in the stream for a sufficient time to reduce or eliminate the amount of contaminant from the stream.

29. The method of Claim 28, wherein the binder includes colloidal aluminum oxide.

The method of Claim 28, wherein the binder includes colloidal silicon dioxide.

31. The method of Claim 28, wherein the binder is cross-linked with itself.

32. The method of Claim 28, wherein the binder is cross-linked with the first particle.

33. The method of Claim 28, wherein the binder is cross-linked with itself and the first particle.

34. The method of Claim 28, wherein the first particle includes an oxide particle or activated carbon.

The method of Claim 28, wherein the first particle includes an oxide of metal, an oxide of silicon or activated carbon.

36. The method of Claim 28, wherein the first particle includes aluminum oxide, titanium dioxide, copper oxide, vanadium pentoxide, silicon dioxide, manganese dioxide, iron oxide, zinc oxide, activated carbon, or zeolite.

37. The method of Claim 28, wherein the first particle includes aluminum oxide. *.o

38. The method of Claim 37, further including a second particle of titanium dioxide, copper oxide, vanadium pentoxide, silicon dioxide, manganese dioxide, iron oxide, zinc oxide, activated carbon, or zeolite. a.Q

39. The method of Claim 28, wherein the first particle includes aluminum oxide and activated carbon.

40. The method of Claim 39, wherein the first particle further includes silicon dioxide and wherein the activated carbon is a mixture of coal based and coconut based activated carbon.

41. The method of Claim 28, wherein the binder is from 20 to 99% by weight of the particle.

42. The binder of Claim 1, wherein the acid includes nitric acid, sulfuric acid, hydrochloric acid, acetic acid, formic acid, phosphoric acid, or a mixture thereof. 36

43. A binder including colloidal aluminum oxide or colloidal silicon dioxide and an acid for binding-adsorbent and/or catalytic particle to produce an agglomerated particle. Dated this 3rd day of May 1999 M AND K PATENT COMPANY, INC. By their Patent Attorneys GRIFFITH HACK Fellows Institute of Patent and Trade Mark Attorneys of Australia 4 4 o« o