WO1991017828A1 - Catalyseurs de destruction de matieres organiques halogenees - Google Patents

Catalyseurs de destruction de matieres organiques halogenees Download PDF

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Publication number
WO1991017828A1
WO1991017828A1 PCT/US1991/003372 US9103372W WO9117828A1 WO 1991017828 A1 WO1991017828 A1 WO 1991017828A1 US 9103372 W US9103372 W US 9103372W WO 9117828 A1 WO9117828 A1 WO 9117828A1
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Prior art keywords
metal
impregnating
compound
binder
zeolite
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PCT/US1991/003372
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English (en)
Inventor
Howard L. Greene
Sougato Chatterjee
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The University Of Akron
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Priority to AU80961/91A priority Critical patent/AU8096191A/en
Priority to DE69121711T priority patent/DE69121711D1/de
Priority to EP91910943A priority patent/EP0528982B1/fr
Publication of WO1991017828A1 publication Critical patent/WO1991017828A1/fr

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    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/30—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
    • A62D3/38—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by oxidation; by combustion
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • 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
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00—Catalysts comprising molecular sieves
    • B01J29/04—Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/061—Crystalline aluminosilicate zeolites; Isomorphous compounds thereof containing metallic elements added to the zeolite
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/0009—Use of binding agents; Moulding; Pressing; Powdering; Granulating; Addition of materials ameliorating the mechanical properties of the product catalyst
    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20—Organic substances
    • A62D2101/22—Organic substances containing halogen
    • A—HUMAN NECESSITIES
    • A62—LIFE-SAVING; FIRE-FIGHTING
    • A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20—Organic substances
    • A62D2101/28—Organic substances containing oxygen, sulfur, selenium or tellurium, i.e. chalcogen
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • 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]

Definitions

  • This invention relates to metal-exchanged, metal- impregnated zeolite catalysts for the destruction of halogenated organics, said catalysts being supported or unsupported, optionally containing a binder, a process for making said catalysts and a process for the oxidative destruction of hazardous halogenated organics including chlorinated hydrocarbons, fluorinated hydrocarbons, and fluoro-chloro carbons (CFC's) which comprises burning the halogenated organics in the presence of said catalysts in an excess of oxygen or an oxygen containing gas mixture such as air.
  • CFC's fluoro-chloro carbons
  • Halogenated organics including volatile and non ⁇ volatile chlorinated, fluorinated and chloro-fluoro hydrocarbons, represent a considerable health and environmental risk.
  • the destruction of these compounds normally requires high temperature oxidation in the presence of a supported catalyst such as chromium oxide supported on alumina or other types of supports.
  • Hunter et al. in U.S. Patent 4,330,513 has reported a process using a fluid bed reactor and chromium oxide catalyst impregnated on alumina for a process for burning catalytically chlorinated hydrocarbons including polychlorinated biphenyls (PCB) .
  • PCB polychlorinated biphenyls
  • His apparatus requires a continuously fluidized bed of catalytic particles and is accomplished at a temperature range between 460°C - 745°C.
  • Hyatt teaches the use of a copper exchanged zeolite in a process to recover chlorine values from essentially perchlorinated hydrocarbons. This reaction involves the controlled oxidation of the chlorinated hydrocarbons in such a way as to optimize the recovery of chlorine gas.
  • the invention was primarily geared toward the recovery of chlorine from the bottoms (high boiling by-products) produced during certain chlorination reactions.
  • the above catalysts and processes involve either the use of exchanged zeolites for oxidation of chlorinated organics or the use of metal-exchanged zeolites or metal- impregnated zeolites for the recovery of chlorine from essentially perchlorinated hydrocarbons. Further, the above processes dealt mostly with fluidized reactors and fluidizable catalysts. Therefore, the catalysts were normally in the form of pure zeolite powders or finely divided particulates not suitable for fixed bed reactors.
  • a further object of this invention is to provide a process for manufacturing the catalyst of the present invention.
  • a still further object of this invention is to provide a process for the oxidative destruction of halogenated organics on the catalysts of the present invention in a temperature range from about 100°C to about 650°C and preferably from about 150°C and 450°C.
  • This invention relates to a metal-exchanged, metal- impregnated zeolite catalyst for the destruction of halogenated organics, said catalyst being supported or unsupported, comprising from 0 weight percent, hereinafter wt.%, to about 95 wt.% of a binder, from about 10 wt.% to about 95 wt.% of a metal-exchanged zeolite, and from about 0.2 wt.% to about 12 wt.% of an impregnating metal compound, said percentage being calculated as the metal loading on an oxide basis, where the metal in the metal-exchanged zeolite can be selected from the representative and illustrative group consisting of V, Cr, Co, Ni, Cu, Fe, Mo, and Mn and the impregnating metal compound can be selected from the representative and illustrative group consisting of compounds of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd, and Pt.
  • a process for making said catalysts and a process for the oxidative destruction of hazardous halogenated organics including chlorinated hydrocarbons, fluorinated hydrocarbons, and fluoro-chloro carbons (CFC's) which comprises burning the halogenated organics in the presence of said catalyst and the excess of oxygen or an oxygen containing gas mixture such as air.
  • hazardous halogenated organics including chlorinated hydrocarbons, fluorinated hydrocarbons, and fluoro-chloro carbons (CFC's) which comprises burning the halogenated organics in the presence of said catalyst and the excess of oxygen or an oxygen containing gas mixture such as air.
  • this invention relates to a metal- exchanged, metal-impregnated zeolite catalyst for the oxidative destruction of hazardous halogenated organics with oxygen or an oxygen containing gas mixture such as air, preferably in excess, the catalyst being supported or unsupported, which comprises from about 5 wt.% to about 25 wt.% of a binder, from about 63 wt.% to about 93 wt.% of a metal-exchanged zeolite, and from about 2 wt.% to about 12 wt.% of an impregnating metal compound.
  • this invention relates to a metal- exchanged, metal-impregnated zeolite catalyst for the oxidative destruction of hazardous halogenated organics with oxygen or an oxygen containing gas mixture such as air, preferably in excess, the catalyst being supported or unsupported, which comprises from about 88 wt.% to about 98 wt.% of a metal-exchanged zeolite, and from about 2 wt.% to about 12 wt.% of an impregnating metal compound.
  • this invention relates to a metal- exchanged, metal-impregnated zeolite catalyst for the oxidative destruction of hazardous halogenated organics with oxygen or an oxygen containing gas mixture such as air, preferably in excess, where the catalyst is washcoated onto a support, which comprises from about 30 wt.% to about 46 wt.% of a binder, from about 42 wt.% to about 68 wt.% of a metal-exchanged zeolite, and from about 2 wt.% to about 12 wt.% of an impregnating metal compound.
  • this invention relates to a metal- exchanged zeolite, finely powdered impregnating compound catalyst for the oxidative destruction of hazardous halogenated organics with oxygen or an oxygen containing gas mixture such as air, preferably in excess, the catalyst being supported or unsupported, which comprises from about 5 wt.% to about 40 wt.% of a binder, from about 10 wt.% to about 80 wt.% of a metal-exchanged zeolite, and from about 2 wt.% to about 12 wt.% of an impregnating metal compound.
  • the binder which need not be present, can be selected from the representative and illustrative group consisting of alumina, silica, alumina-silica, cordierite, titania, zirconia, vanadia, and other inorganic materials used as binding agents.
  • binders such as Silbond * or other binders which form high surface area matrices are preferred. While not wishing to be bound by theory, it is believed that the binder, when present, will act as a bonding agent to secure the metal-exchanged zeolite onto the support, and also acts as a surface which will bond with the impregnating agent.
  • the metal in the metal-exchanged zeolite can be selected from the representative and illustrative group consisting of V, Cr, Co, Ni, Cu, Fe, Mo, and Mn.
  • the impregnating metal compound can be selected from the representative and illustrative group consisting of compounds of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd, and Pt.
  • the impregnating metal compound is a water soluble metal compound where the metal is available as an ion in any allowable oxidation state.
  • the support can be made of any standard support material such as, but not restricted to.
  • the support can be in any desirable shape including, but are not restricted to, honeycomb, monolith, pellets, rings, spheres, saddles, ceramic foams, extrudates, or other types of shaped support. Honeycombs and monoliths are preferred.
  • the metal- exchanged, metal-impregnated zeolite of the instant invention can be prepared by a process which comprises the steps of: (1) exchanging a zeolite with a metal to form a metal-exchanged zeolite; (2) drying the metal-exchanged zeolite; (3) calcining the metal-exchanged zeolite, (4) optionally adding a binder to the metal-exchanged zeolite; (5) drying the metal-exchanged zeolite/binder combination, if the binder is present; (6) calcining the metal-exchanged zeolite/binder combination, if the binder is present; (7) impregnating the metal-exchanged zeolite to form a metal- exchanged zeolite, metal-impregnated catalyst; (8) drying the metal-exchanged, metal-impregnated catalyst; and (9) calcining the metal-impregnated, metal-exchanged zeolite catalyst to
  • the metal- exchanged, metal-impregnated zeolite of the instant invention can be prepared by a process which comprises the steps of: (1) exchanging a zeolite with a metal to form a metal-exchanged zeolite; (2) drying the metal-exchanged zeolite; (3) calcining the metal-exchanged zeolite, (4) washcoating the metal-exchanged zeolite catalyst onto an inorganic support with or without a binder; (5) drying the washcoated metal-exchanged zeolite/support combination; (6) calcining the washcoated metal-exchanged zeolite/support combination; (7) impregnating the metal-exchanged washcoated zeolite/support to form a metal-exchanged zeolite, metal- impregnated catalyst; (8) drying the metal-exchanged, metal- impregnated catalyst; and (9) calcining the metal- impregnated, metal-exchanged zeo
  • the metal- exchanged, metal-impregnated zeolite of the instant invention can be prepared by a process which comprises the steps of: (1) exchanging a zeolite with a metal to form a metal-exchanged zeolite; (2) drying the metal-exchanged zeolite; (3) calcining the metal-exchanged zeolite, (4) dry-mixing the metal-exchanged zeolite powder with a finely powdered impregnating metal compound, (5) adding a binder to form a metal-exchanged zeolite, finely powdered impregnating metal compound powder/binder slurry, (6) drying the metal- exchanged zeolite, finely powdered impregnating metal compound/binder slurry; and (7) calcining the metal- exchanged zeolite, finely powdered impregnating metal compound catalyst to form an active catalyst for the destruction of halogenated organics.
  • Exchanging a zeolite with a metal which is typically a water soluble metal salt with the metal available as an ion, to form a metal-exchanged zeolite, normally involves first treating the zeolite with ammonia in an aqueous environment to convert protonic sites to ammonium sites; the ammonium sites facilitating the metal exchange reaction.
  • water soluble metal salts are used in the exchange reaction because the exchange reaction involves the replacement or exchange of one ion for another ion in the channels or cages of the zeolite.
  • the exchange process is normally carried out until exchange equilibrium is attained which can range from about six hours to about 24 hours or more, with 10 to 20 hours being preferred.
  • Washcoating is a technique for surface deposition of an active catalyst species onto the surface of an inert support.
  • the coating technique is normally performed by dipping a support in a slurry of the active catalyst and optionally a binder.
  • the binder when necessary, allows efficient adherence of the catalytic agent to the support surface. Drying and calcining completes the washcoat bonding process resulting in a surface coated support.
  • the coverage of the surface will not be complete, and second, that pores formed by the binder can expose zeolite or support.
  • the amount of the catalytic composition, washcoated or otherwise bonded to the surface of a given support will depend in a large part on the end use of the particular supported catalysts. However, typically, the catalyst composition does not make up more than 50% of the weight of the final catalyst, i.e., 50% catalyst and 50% support. Preferably, the catalyst compositions make up no more than 25% of the combined weight. However, supported catalysts can be made where the catalyst composition makes up more than 50% of the weight or less than 25% of the weight.
  • Impregnation is a technique where a surface is saturated with a metal ion.
  • the impregnating metal compound can be selected from the representative and illustrative group consisting of compounds of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd, and Pt.
  • the impregnating metal compound can be any reagent containing the desired metal in a usable form, such as, but not restricted to, water soluble salts of these metals where the metal ion is in any chemically allowable oxidation state.
  • the impregnation involves immersion or soaking of the washcoated catalyst in a solution containing the impregnating metal compound, and optionally a binder.
  • the impregnated catalyst is then subjected to a drying and a calcining step.
  • the impregnation step is normally performed in an aqueous medium which requires the impregnating metal compound to be water soluble to some extent.
  • Previously exchanged metal ions are neither lost nor are they replaced during this impregnation process.
  • impregnation sites yield very different catalytic properties from metal-exchanged sites as is subsequently demonstrated by results shown in Figure 1. Comparing the curves for that of a metal-exchanged zeolite, curves for Co-Y, Mn-Y, and Cr-Y, with those for Co-Y/CA, Mn- Y/CA, and Cr-Y/CA, quickly points out these differences.
  • the drying steps are well known drying and are typically performed at a temperature sufficient to promote drying and for a time sufficient to attain drying at a given temperature.
  • temperature of drying and time of drying i.e., as the temperature goes up the time of drying goes down.
  • too rapid a drying rate can adversely affect ultimate catalyst properties.
  • the time and temperature of drying are typically balanced to give the best overall properties.
  • the drying time is usually from about 2 hours to about 48 hours or longer and the drying temperature is usually from about 95°C to about 250°C.
  • the dried catalyst is then calcined at a temperature from about 400°C to about 750°C for a time sufficient to render the catalyst in a stable form from about 2 hours to about 48 hours or longer. Since zeolites are involved, temperatures much above 750°C may cause destruction of the crystalline nature of the zeolite. The thermal destruction of synthetic zeolite is well known in the art.
  • non-supported metal-exchanged, metal-impregnated catalysts there are several methods which can be employed to prepare non-supported metal-exchanged, metal-impregnated catalysts.
  • commercially available zeolite pellets are exchanged with appropriate metal ions.
  • these metal- ion exchanged zeolite pellets are impregnated with a suitable impregnating agent, and optionally with a binder.
  • a non-supported catalyst has been prepared.
  • zeolite powders are exchanged with appropriate metal ions. Subsequent to appropriate drying and calcining, these metal- ion exchanged zeolite powders, are dry-mixed with a suitable finely powdered impregnating metal compound and slurried with a binder. After appropriate drying and calcination steps, followed by sieving to appropriate screen size, a non-supported catalyst has been prepared.
  • non-supported catalysts can also be prepared by simply taking the catalytic mixture (metal- impregnated and metal-exchanged zeolite) and shaping the mixture into a form in a wetted state (inclusion of sufficient water to render the mixture for able, i.e., not too fluid or not too dry, as is well known in the art) , and drying and calcining the form. This process results in a stable, unsupported catalyst.
  • This method may also require the inclusion of extrusion aids such as inorganic or organic plasticizers well known in the art or pore forming additives also well known in the art.
  • non-supported catalysts can be prepared by a method which involves the preparation of a ceramic foam, comprising a mixture of the metal-impregnated and the metal-exchanged zeolite.
  • a ceramic foam comprising a mixture of the metal-impregnated and the metal-exchanged zeolite.
  • the above mixture is sprayed or otherwise coated onto an organic form.
  • the coated form is dried and then calcined, which destroys the organic form, leaving behind a ceramic remnant of the organic form, i.e., a ceramic foam.
  • a ceramic foam i.e., a ceramic foam.
  • metal reagents which can be used for either exchanging the zeolite or for impregnating the catalysts include, but are not restricted to, chlorides including all possible chlorides of each metal, oxides, phosphates, sulfates, acetates, formates, nitrates, bromides, carbonates, hydroxides, and other similar water soluble salts of metals selected from the representative and illustrative group consisting of Ti, V, Cr, Mn, Co, Ni, Cu, Fe, Mo, Mn, Pd and Pt.
  • non-aqueous methods can also be employed to exchange the zeolite or impregnate the washcoated support.
  • the zeolites usable in this invention include pellets and powders, such as Na-Y and H-Y, and are commercially available from Union Carbide, Linde Division, under the tradename Y-52, and Y-82 respectively.
  • Y-zeolites from any other manufacturer can be utilized under similar conditions, along with other types of zeolites, such as A, L, 0, P or X zeolites, silicalites, ZSM series, or naturally occurring zeolites such as faujasites or ordenites.
  • supports can be used as substrates for the catalysts of the present invention.
  • the supports include, but are not restricted to, typical inorganic supports such as alumina, aluminum oxide, silica, silicates, silica- aluminas, aluminum-silicates, titanias, cordierite and other similar supports and combinations thereof.
  • These inorganic supports can be in any number of shapes and structures depending on the exact requirements of the reactor or process in which they will be incorporated.
  • a preferred support shape is the honeycombed type shape. Each honeycomb pattern selected is again a matter of discretion depending to a large extent on the reactor and process variables.
  • shaped forms are also usable including, but not restricted to, spheres, Intalox" saddles, Super Intalox” saddles, Berl saddles, slotted ring Tower Packing", Raschig Rings", cross-partition rings, Lessing rings, balls, pellets, bricks, ceramic foams and monoliths. It has also been possible to use metals, such as stainless steel as a support material.
  • the process for the oxidation of halogenated organics involves contacting the halogenated organics with a catalyst of the present invention in the presence of oxygen or an oxygen containing gas mixture, preferably in excess, at a temperature from about 100°C to about 650°C, preferably from about 150°C to about 450°C, for a time sufficient to fully oxidize the halogenated organics.
  • the time can range from about 0.01 seconds to about 20 seconds, but preferably from about 0.2 to 1.0 seconds.
  • the oxidation is also preferably carried out in the presence of water vapor.
  • the presence of water vapor aids in the oxidation reaction suppressing the formation of halogen gas.
  • the advantage of water vapor also makes destruction of waste organics more amenable to industrial applications where water is normally associated with the waste organics.
  • the destruction of these halogenated organics can occur in the presence of excess oxygen or in an oxygen containing gas including compressed air, compressed oxygen or mixtures thereof.
  • the reaction can be carried out at oxygen ratios near stoichiometry to excesses between 25% and 50% or more. When air-stripping chlorinated contaminants from ground water, the reaction is carried out at an oxygen ratio approximating an excess of 1200%.
  • chlorinated hydrocarbons such as chlorinated methanes including chloromethane, dichloromethane, chloroform, carbon tetrachloride; chlorinated ethane including chloroethane, dichloroethane, trichloroethane, tetrachloroethane and higher chlorinated ethanes; other chlorinated alkanes; chlorinated ethylenes including monochloroethylene, dichloroethylene, trichloroethylene, and tetrachloroethylene; chlorinated propylene and other chlorinated alkenes and dienes; chlorinated aromatics including chlorinated benzenes; perchlorinated hydrocarbons including hexachlorobenzene, hexachlorobutadiene, hexachloroet ane, chlorinated styrenes
  • chlorinated hydrocarbons such as chlorinated methanes including chloromethane, dichloromethane, chloroform, carbon
  • metal-exchanged, metal- impregnated zeolites give rise to unique, highly active, very selective catalysts for the oxidative destruction of halogenated organics to the halo acid and carbon oxides (carbon monoxide and carbon dioxide) . It is believed that these catalysts are novel in that they combine the cracking and oxidation capability of a metal-exchanged zeolite, wherein the first catalytic site in the composition is in a channel or a cage of the zeolite, with the deep oxidation potential of a transition metal oxide, wherein the second catalytic site in the composition is on a surface of the combination. While not wishing to be tied to any theory, it is believed that this combination of first and second site interaction leads to highly active, very selective catalysts for the complete oxidative destruction of halogenated organics to the halo acid and carbon oxides.
  • this invention produces a catalyst resistant to deactivation, common to pure zeolites, as caused by deposition of carbon in the catalyst channels and pores. Instead, the carbon is oxidized primarily to C0 2 and CO.
  • the metal ions used in the zeolitic ion-exchange are selected from the representative and illustrative group consisting of V, Cr, Co, Ni, Cu, Fe, Mo, and Mn .
  • This catalyst is subsequently impregnated with a metal compound where the metal ions used in the metal impregnation are selected from the representative and illustrative group consisting of compounds of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd, and Pt.
  • These catalysts show considerable activity at moderate temperatures typically in the range between approximately 100°C to 650°C and in a particularly preferred range of approximately 150°C to about 450°C.
  • the catalysts are active enough to oxidize the halogenated organic feeds coming into it in very short periods of time, ranging from approximately .01 second to approximately 20 seconds.
  • This metal-exchanged, metal- impregnated catalyst shows marked increases in both reactivity and selectivity over its non-impregnated analog, which only has metal catalytic sites available in the channels and cages of the zeolite.
  • the metal-exchanged, metal-impregnated zeolite catalyst is typically prepared by first ammonium exchanging the zeolite, followed by the exchange of the ammonium group with the active metal agent.
  • zeolites that have already been ammonium exchanged can be used directly without prior ammonium treatment.
  • Non-ammonium exchanged zeolites can also be used, but the exchange reaction does not proceed as well.
  • the preferred chromium exchange salt is chromic nitrate.
  • other water soluble chromium salts can be used to affect the exchange.
  • ammonium- exchanged zeolite where the protonic acid sites of the original zeolites have been exchanged or reacted by ammonium, provides a more efficient procedure for the exchange of an active zeolite site within the zeolitic channel and cages by the chromium ions.
  • This same technique works equally well with soluble salts of V, Co, Ni, Cu, Fe, Mo, and Mn.
  • the metal-exchanged zeolite is then dried and calcined under conditions to attain a stable and active zeolite. Zeolites can be destroyed by calcining either at too high of a temperature or at a temperature close to the zeolite destruction temperature for too long a time during calcining.
  • the metal-exchanged zeolite is then washcoated onto an inorganic support which has been etched to facilitate the binding.
  • etching is not mandatory and is used only to improve binding.
  • the washcoating is optionally performed in the presence of an inorganic binder such as Silbond-H-5 * .
  • alumina binders are preferred when fluorinated organics are a part of the waste product composition that is to be oxidized in the presence of the catalysts described herein. This requirement is probably due to the volatility of SiF 4 formed during oxidation of fluorocarbons in the presence of silica. Alumina is not susceptible to the formation of volatile fluorides.
  • the silica or alumina binder if necessary, is used to aid in binding the zeolite to the surface of the inorganic support which is effectuated by a calcination step which allows the binder to bond the zeolite to the surface of the inorganic support producing a zeolite coated support.
  • Washcoating binders also produce pores on the surface of the support.
  • the pores can expose zeolite or support surfaces.
  • the optional binder by producing pores on the surface of the support, also typically increases the surface area of the resulting catalytic composition.
  • the invention describes a single washcoating, multiple washcoatings can be used as well. Repeating the washcoating process simply increases the amount of active zeolite on the surface.
  • any type of support commonly used in the art would be suitable for the present application as well as binders commonly known in the art.
  • the washcoated inorganic support or preformed binder/zeolite catalyst is impregnated with an impregnating metal compound, where the metal in the metal-exchanged zeolite can be selected from the representative and illustrative group consisting of V, Cr, Co, Ni, Cu, Fe, Mo, and Mn and the impregnating metal compound can be selected from the representative and illustrative group consisting of compounds of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd, and Pt.
  • the amount of impregnating metal compound can range from about 0.2 wt.% to about 12 wt.%, preferably from about 2 wt.% to about 12 wt.% based on the combined weight of the catalyst composition which does not include the weight of the support.
  • the impregnation uses a soluble metal compound to effect an aqueous impregnation of the washcoated support.
  • the impregnating metal compound is allowed to impregnate the surface of the zeolite and if present, the surface of the binding agent to form metal sites other than the zeolitic channel and cage metal sites. It is thought that the combination of these two different types of metal sites is responsible for the significantly increased reactivity and selectivity of this catalyst.
  • the ability to make the metal in the zeolite different from the metal impregnated into the zeolite surface allows considerable flexibility in making and utilizing these catalysts. This ability also allows for the design of catalyst more specifically tailored to destroy different classes of organic wastes.
  • the preferred compound is chromic acid.
  • drying and calcining are required to bond the impregnating metal compound on the catalytic surface and render stable active catalytic sites.
  • Multiple impregnations are also obvious extensions of the present teaching and is a simple technique for increasing the amount of secondary catalytic sites on the zeolite surface.
  • the metal-exchanged zeolite is optionally slurried into an inorganic binder such as Silbond-H-5 * to facilitate the impregnating metal binding.
  • alumina binders are preferred when fluorinated organics are a part of the waste product composition that is to be oxidized in the presence of the catalysts described herein. This requirement is probably due to the volatility of SiF 4 formed during oxidation of fluorocarbons in the presence of silica. Alumina is not susceptible to the formation of volatile fluorides.
  • the silica or alumina binder if necessary, is used to aid in binding the impregnating metal to the surface of the inorganic support which is effectuated by a drying/calcination step which allows the binder to adhere to the zeolite. Binders also produce pores on the surface. Producing pores on the surface of the support, also typically increases the surface area of the resulting catalytic composition.
  • the metal-exchanged zeolite and optional binder is impregnated with an impregnating metal compound, where the metal in the metal-exchanged zeolite can be selected from the representative and illustrative group consisting of V, Cr, Co, Ni, Cu, Fe, Mo, and Mn and the impregnating metal compound can be selected from the representative and illustrative group consisting of compounds of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd, and Pt.
  • the amount of impregnating metal compound can range from about 0.2 wt.% to about 12 wt.%, preferably from about 2 wt.% to about 12 wt.% based on the combined weight of the catalyst composition which does not include the weight of the support.
  • the impregnation uses a soluble metal compound to effect an aqueous impregnation of the washcoated support.
  • the impregnating metal compound is allowed to impregnate the surface of the zeolite and if present, the surface of the binding agent to form metal sites other than the zeolitic channel and cage metal sites. It is thought that the combination of these two different types of metal sites is responsible for the significantly increased reactivity and selectivity of this catalyst.
  • the ability to make the metal in the zeolite different from the metal impregnated into the zeolite surface allows considerable flexibility in making and utilizing these catalysts. This ability also allows for the design of catalyst more specifically tailored to destroy different classes of organic wastes.
  • the metal-exchanged zeolite is dry-mixed with a finely divided metal impregnating compound and slurried into an inorganic binder such as Silbond-H-5" to facilitate the zeolite/impregnating metal compound binding.
  • alumina binders are preferred when fluorinated organics are a part of the waste product composition that is to be oxidized in the presence of the catalysts described herein. This requirement is probably due to the volatility of SiF 4 formed during oxidation of fluoro ⁇ arbons in the presence of silica. Alumina is not susceptible to the formation of volatile fluorides.
  • the silica or alumina binder if necessary, is used to aid in binding the impregnating metal to the surface of the inorganic support which is effectuated by a drying/calcination step which allows the binder to adhere to the zeolite. Binders also produce pores on the surface. Producing pores on the surface of the support, also typically increases the surface area of the resulting catalytic composition.
  • the metal-exchanged metal-impregnated zeolite catalyst is such that the metal in the metal-exchanged zeolite can be selected from the representative and illustrative group consisting of V, Cr, Co, Ni, Cu, Fe, Mo, and Mn and the impregnating metal compound can be selected from the representative and illustrative group consisting of compounds of Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd, and Pt.
  • the amount of impregnating metal compound can range from about 0.2 wt.% to about 12 wt.%, preferably from about 2 wt.% to about 12 wt.% based on the combined weight of the catalyst composition which does not include the weight of the support.
  • the impregnation uses a metal compound which has some degree of solubility in the inorganic binder, such as Silbond-H-5", to effect an aqueous impregnation of the washcoated support.
  • the impregnating metal compound is allowed to impregnate the surface of the zeolite and the surface of the binding agent to form metal sites other than the zeolitic channel and cage metal sites. It is thought that the combination of these two different types of metal sites is responsible for the significantly increased reactivity and selectivity of this catalyst.
  • the ability to make the metal in the zeolite different from the metal impregnated into the zeolite surface allows considerable flexibility in making and utilizing these catalysts. This ability also allows for the design of catalyst more specifically tailored to destroy different classes of organic wastes.
  • This example describes the preconditioning of the inorganic support. This step is optional and is presented here only to indicate the manner in which the catalyst was prepared in full.
  • a three-inch cordierite core was leached in a 1.5 N aqueous HN0 3 solution at 95°C for about two and a half hours, followed by washing with distilled water for 10 minutes at 95°C. This resulted in a core with a weight loss in the vicinity of 2-6%.
  • the leached core was dried in an oven at 100°C for 10-16 hours.
  • This example describes the preparation of a chromium- exchanged zeolite.
  • the resulting zeolite aggregate was crushed to a fine powder and used for washcoated catalyst preparation.
  • this example involves Cr exchange, the exact procedure can be used for the other metals taught herein. The only difference would be in the replacement of Cr(N0 3 ) 3 with a similar salt of either V, Co, Ni, Cu, Fe, Mo, and Mn.
  • This example describes the washcoating procedure for depositing the chromium exchanged zeolite onto an inorganic suppor .
  • Example 2 Approximately 25% by weight, based on the amount of binder of the exchanged zeolite of Example 2 , was slurried in 200 ml of Silbond-H-5*. The slurry was kept well mixed by continuous stirring. The weighed cordierite core, as prepared in Example 1, was dipped into the slurry and taken out. The cordierite channels were then partially cleared by blowing compressed air through them. The above procedure was repeated four times. Finally, the core was dried at 200°C for two hours followed by calcination at 550°C for 12- 14 hours. Generally the core showed a weight gain of between 15% and 20% after the washcoating procedure.
  • This example describes the preparation of a CA- impregnated catalyst of Example 3.
  • Approximately 6% salt solution was prepared by dissolving 20 grams of chromium oxide (Cr0 3 ) in 300 ml of distilled deionized water.
  • the catalyst as prepared in Example 3 was immersed into the chromic acid (H 2 CrO solution and kept there for about two hours. Thereafter, the catalyst core was removed and dried at 200°C for two hours. It was then calcined at 550°C for 10-12 hours.
  • This example describes the procedure for preparing unsupported binderless CA-impregnated Co-Y catalyst pellets.
  • 1/16" LZ-Y62 extrudates/pellets were obtained from Union Carbide Co. 100 grams of the Y-62 pellets were ammonium exchanged as per Example 2. The ammonium-exchanged zeolite pellets were slurried in approximately twice their weight of distilled deionized water (120 ml) . 16 grams of Co(N0 3 ) 2 «6H 2 0, based on 3.25 grams of Co per 100 grams of zeolite, was dissolved in approximately 300 times its weight of distilled deionized water. The dilute solution of the exchanging salt Co(N0 3 ) 2 , was added to the zeolite slurry and the resulting mixture was continuously stirred at about 40-50°C.
  • the Co-Y pellets were CA- impregnated by slurrying them in a 13 wt% solution of Cr0 3 in water.
  • the Co-Y pellets were immersed into the chromic acid solution at about 25°C and kept there for 3-4 hours. Thereafter the catalyst pellets were removed and dried at 200°C for two hours. They were then calcined at 550°C for 10-12 hours.
  • the same procedure can be used to impregnate the exchanged zeolites with any other metals taught herein.
  • This example describes the procedure for preparing unsupported CA-impregnated Co-Y catalysts from zeolite powder and a silica binder.
  • Co-Y was prepared by Co exchanging LZ-Y82 zeolite powder as in Examples 2 and 5. Approximately 25% by weight, based on the amount of silica binder, was slurried in 68 ml of Silbond-H-5 * . The slurry was well mixed by continuous stirring and heated to 40°C for about 1 hour. After the required time period, the volatile part of the Silbond-H-5 * evaporated and the slurry became a thick paste. This zeolite/binder paste was dried at 200°C for 2 hours followed by calcining at 550°C for 10-12 hours. After calcining, the Co-Y/Silbond aggregate was crushed and sieved to 3/64" pellets.
  • pellets were further CA-impregnated from a 13 wt% Cr0 3 solution in water as described in Example 5. Even though CA impregnation was carried out in this case, any other suitable metal salts can also be used to do the metal impregnation step.
  • Co-Y was prepared by Co exchanging LZ-Y82 zeolite powder as in Examples 2 and 5. Approximately 9.0 grams of Co-Y zeolite powder was dry-mixed with 0.55 grams of Cr 2 0 3 . After a suitable period of time, 15.0 grams of Silbond-H-5 * was added to the mixed powder to form a slurry. The slurry was well mixed by continuous stirring and heated to 40°C for about 1 hour.
  • the catalyst conditions can be selected to obtain nearly quantitative destruction of the chlorinated hydrocarbon with high chlorine and carbon mass balances.
  • Selectivities to hydrochloric acid and carbon oxides can be co-optimized to approach near quantitative yield of both, which would result in the suppression of the formation of chlorine gas and/or higher chlorinated hydrocarbons.
  • the presence of water insures that the formation of hydrochloric acid is favored over the formation of chlorine gas by shifting the equilibrium of the Deacon reaction to the right:
  • Figures 1 to 6 describe a series of reactor runs using catalysts of Examples 4 - 6 and various volatile chlorinated hydrocarbon feeds including methylene chloride, carbon tetrachloride and tetrachloroethylene under varying conditions including variations in reaction temperature, and feed ratios.
  • the feed ratio is the ratio of the number of carbon-chlorine bonds in the feed to the total number of carbon-chlorine bonds plus the total number of hydrogen atoms present in the feed mixture.
  • the feed ratio is 0.5 (2 C-Cl bonds / (2 C-Cl bonds + 2 hydrogen) ) .
  • the feed ratio is 1.0
  • tetrachloroethylene the feed ratio is 1.0. Feed ratios less than the feed ratio for the pure chlorinated hydrocarbon evidence the addition of water to the feed. The lower the feed ratio (number value) , the more added water.
  • FIGs 3,4 and Figures 5,6 provide comparable data using CC1 4 and MeCl 2 as the feedstocks. While the impregnated, exchanged zeolitic catalysts of the instant invention are not optimal for these feedstocks, it must be noted that chlorinated feeds do not typically occur in isolation. They almost universally occur as extremely complex mixtures of chlorinated moieties. These graphs do exhibit the fact that catalysts of the instant invention will work at low temperatures.
  • Runs 1-9 use a CA-impregnated, Cr-Y washcoated cordierite monolith catalyst; runs 10-18 use a CA-impregnated Cr-Y doubly washcoated cordierite monolith catalyst; runs 19-26 use a doubly-impregnated Cr-Y washcoated cordierite monolith catalyst; runs 27-35 use a CA doubly-impregnated, Cr-Y doubly-washcoated cordierite monolith catalyst; runs 36-40 use a Co-Y treated cordierite monolith catalyst; runs 41-44 use a CA-impregnated, Co-Y washcoated cordierite monolith catalyst; runs 45-49 use a Cu-Y washcoated cordierite monolith catalyst; and runs 50-53 use a CA-impregnated, Cu-Y washcoated cordierite monolith catalyst.
  • Tables 1-9 use a CA-impregnated, Cr-Y washcoated cordierite monolith catalyst
  • runs 10-18 use a CA-impregnated Cr-Y doubly washco
  • Comparing runs 36-40 with 41-44 also shows the substantial improvement that CA impregnation causes, particularly in the case with two-carbon moieties. This same effect is seen in the case of Cu-Y catalyst (runs 45-49 and 50-53) .
  • any chlorinated organic be it volatile or non ⁇ volatile, can be oxidized in an analogous fashion, except that higher boiling chlorinated organics may have to be fed by entrainment or by higher inlet temperatures. Also, it should be recognized that when the halogenated organics contain fluorine, then alumina binders are preferred.
  • Runs 54-57 indicate that even a very stable CFC can be easily and readily destroyed using a catalyst according to Example 4 where the exchanging metal and the impregnating metal compound contain chromium as the active catalytic metal. At a temperature of 475°C approximately 90-95% of CFC-12 is destroyed with high chlorine accountability and reasonably good carbon accountability.
  • Runs 58-60 show that the present catalyst oxidatively destroys CFC-11 at a lower temperature (400°C ) than CFC-12. This fact is due to the stability difference between CFC-12 and CFC-11. The conversion is nearly quantitative at 400°C with good chlorine and carbon balance.

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Abstract

On a préparé une nouvelle classe de catalyseurs à zéolite à échange et à imprégnation de métal utilisés dans l'oxydation de matières organiques halogénées comprenant des hydrocarbures chlorés, fluorés et chloro/fluoro. Ces catalyseurs sont supportés ou non supportés, ils comprennent de 0 pour cent en poids à environ 95 % en poids d'un liant, d'environ 10 % à environ 95 % en poids d'une zéolite à échange de métal, et d'environ 0,2 % à environ 12 % en poids d'un composé de métal d'imprégnation, ledit pourcentage se présentant sous la forme d'un calcul d'accumulation de métal sur une base oxyde. On peut sélectionner le métal se trouvant dans la zéolite à échange de métal dans le groupe représentatif et illustratif composé de V, Cr, Co, Ni, Cu, Fe, Mo et Mn, et on peut sélectionner le composé de métal d'imprégnation dans le groupe représentatif et illustratif comprenant des composés de Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Mo, Pd et Pt. L'invention concerne également un procédé de fabrication des catalyseurs ainsi qu'un procédé d'oxydation des matières organiques halogénées se produisant à des températures relativement basses, entre environ 100 et environ 650 °C, ainsi qu'à des pressions proches de la pression atmosphérique et pendant des temps de séjour compris entre environ 0,01 secondes et environ 20 secondes.
PCT/US1991/003372 1990-05-14 1991-05-14 Catalyseurs de destruction de matieres organiques halogenees WO1991017828A1 (fr)

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AU80961/91A AU8096191A (en) 1990-05-14 1991-05-14 Catalysts for the destruction of halogenated organics
DE69121711T DE69121711D1 (de) 1990-05-14 1991-05-14 Verfahren zum abbau halogenierter organischer substanzen
EP91910943A EP0528982B1 (fr) 1990-05-14 1991-05-14 Procede de destruction de matieres organiques halogenees

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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0645172A1 (fr) * 1993-09-24 1995-03-29 N.E. Chemcat Corporation Méthode et catalyseur pour le traitement des effluents gazeux contenant des dioxines
WO1995011726A1 (fr) * 1993-10-27 1995-05-04 The University Of Akron Catalyseurs d'oxydation selective pour composes organiques halogenes
WO1995011727A1 (fr) * 1993-10-27 1995-05-04 The University Of Akron Systeme combine de catalyseur/sorbant
WO1996030085A1 (fr) * 1995-03-30 1996-10-03 Nuclear Fuels Plc British Oxydation catalytique
EP0908221A1 (fr) * 1997-09-16 1999-04-14 Siemens Aktiengesellschaft Catalyseur et procédé pour la réduction des dioxines à basse température
US6589495B2 (en) 1998-11-09 2003-07-08 Siemens Aktiengesellschaft Process for reducing the levels of halogenated hydrocarbons
US6790363B2 (en) 2001-07-24 2004-09-14 Chk Group, Inc. Method of treating arsenic-contaminated waters
CN112588289A (zh) * 2020-12-01 2021-04-02 光大环境修复(江苏)有限公司 一种高CO2选择性的脱CVOCs催化剂及其制备方法

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3004906A (en) * 1956-11-09 1961-10-17 North American Aviation Inc Uranium foil nuclear fuel element
US3218363A (en) * 1956-08-15 1965-11-16 Pennsalt Chemicals Corp Purification of perfluorochlorocarbons
US3328316A (en) * 1966-01-24 1967-06-27 Chevron Res Method of depositing metals on siliceous supports
US3989806A (en) * 1975-02-10 1976-11-02 Vulcan Materials Company Low temperature catalytic oxidation of chlorinated organic compounds to recover chlorine values
US3989807A (en) * 1975-02-10 1976-11-02 Vulcan Materials Company Low temperature catalytic oxidation of chlorinated compounds to recover chlorine values using chromium-impregnated supported catalysts
US4330513A (en) * 1976-10-13 1982-05-18 Air Resources, Inc. Catalytic fume incineration
US4358428A (en) * 1975-12-24 1982-11-09 Ngk Insulators, Ltd. Method of removing nitrogen oxides from waste gas by selective contact reduction
US4423024A (en) * 1980-03-11 1983-12-27 The Dow Chemical Company Selective conversion of chlorinated alkanes to hydrogen chloride and carbon dioxide
US4916096A (en) * 1986-05-30 1990-04-10 Shell Oil Company Hydrocarbon conversion catalysts

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3218363A (en) * 1956-08-15 1965-11-16 Pennsalt Chemicals Corp Purification of perfluorochlorocarbons
US3004906A (en) * 1956-11-09 1961-10-17 North American Aviation Inc Uranium foil nuclear fuel element
US3328316A (en) * 1966-01-24 1967-06-27 Chevron Res Method of depositing metals on siliceous supports
US3989806A (en) * 1975-02-10 1976-11-02 Vulcan Materials Company Low temperature catalytic oxidation of chlorinated organic compounds to recover chlorine values
US3989807A (en) * 1975-02-10 1976-11-02 Vulcan Materials Company Low temperature catalytic oxidation of chlorinated compounds to recover chlorine values using chromium-impregnated supported catalysts
US4358428A (en) * 1975-12-24 1982-11-09 Ngk Insulators, Ltd. Method of removing nitrogen oxides from waste gas by selective contact reduction
US4330513A (en) * 1976-10-13 1982-05-18 Air Resources, Inc. Catalytic fume incineration
US4423024A (en) * 1980-03-11 1983-12-27 The Dow Chemical Company Selective conversion of chlorinated alkanes to hydrogen chloride and carbon dioxide
US4916096A (en) * 1986-05-30 1990-04-10 Shell Oil Company Hydrocarbon conversion catalysts

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See also references of EP0528982A4 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0645172A1 (fr) * 1993-09-24 1995-03-29 N.E. Chemcat Corporation Méthode et catalyseur pour le traitement des effluents gazeux contenant des dioxines
WO1995011726A1 (fr) * 1993-10-27 1995-05-04 The University Of Akron Catalyseurs d'oxydation selective pour composes organiques halogenes
WO1995011727A1 (fr) * 1993-10-27 1995-05-04 The University Of Akron Systeme combine de catalyseur/sorbant
WO1996030085A1 (fr) * 1995-03-30 1996-10-03 Nuclear Fuels Plc British Oxydation catalytique
US6224841B1 (en) 1995-03-30 2001-05-01 British Nuclear Fuels Lc Catalytic oxidation
EP0908221A1 (fr) * 1997-09-16 1999-04-14 Siemens Aktiengesellschaft Catalyseur et procédé pour la réduction des dioxines à basse température
US6589495B2 (en) 1998-11-09 2003-07-08 Siemens Aktiengesellschaft Process for reducing the levels of halogenated hydrocarbons
US6790363B2 (en) 2001-07-24 2004-09-14 Chk Group, Inc. Method of treating arsenic-contaminated waters
CN112588289A (zh) * 2020-12-01 2021-04-02 光大环境修复(江苏)有限公司 一种高CO2选择性的脱CVOCs催化剂及其制备方法

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