Plaque It!
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[0001] As internal combustion engines wear, the annular spaces between the pistons and the cylinder tend to increase. In the combustion chamber of each cylinder, an air-fuel mixture is ignited. The expanding gas mixture forces the piston upwards generating power from the engine. In the expansion process, part of the gas mixture is forced between the annular spaces between the piston and the cylinder into the crankcase. These “blow-by” gases, which also include oil mist and unburned fuel, accumulate in the crankcase and must be vented from the crankcase to the atmosphere to prevent a potentially dangerous pressure build-up in the crankcase. In addition, unburned fuel can be present in the combustion chambers after the internal combustion engine is shut down. These hydrocarbons cannot get to the crankcase without the pistons moving, but they may escape through open valves and migrate back through the air intake system. In addition, the activated carbon canister may release significant amounts of stored hydrocarbons when a vehicle has not run for a number of days.
[0002] Pollution control laws and regulations restrict the emissions from internal combustion engines. As exhaust gases from internal combustion engines have become cleaner, the blow-by gases and evaporative emissions have become a more significant fraction of the total pollution generated from internal combustion engines. In many localities, the pollution control laws and regulations are such that vapors from the internal combustion engines must be cleaned prior to discharge into the atmosphere. The current evaporative emissions requirements require emissions of less than 2.0 grams of fuel vapor over a one-hour test period. It is expected that these requirements will change in the year 2004 to requiring emissions of less than 2.0 grams fuel vapor over a three day test period.
[0003] Disclosed herein is an air cleaner assembly, an adsorber member, and a process for reducing pollutants from being discharged into the atmosphere.
[0004] The air cleaner assembly comprises a housing comprising a filter element situated therein, an outlet for allowing filtered air to flow to the engine, and an inlet conduit extending from the housing for permitting the entry of air into the housing; a retainer coupled to the inlet conduit, the retainer comprising a wall defining a first open end and a second open end, wherein the wall forms a cuffed portion about the second open end and has an annular recess facing the first open end, wherein a portion of an annular wall of the inlet conduit is seated in the recess; a clamping device disposed about the second open end and the portion of the annular wall to provide an air tight seal between the retainer and housing coupling; and an adsorber member sealingly disposed within the first open end, wherein the adsorber member comprises a silicate adsorbing material free from a zeolite material.
[0005] The adsorber member comprises a support comprising a plurality of fluid passageways; and a silicate pollutant treating material free from zeolite disposed onto a surface of the support. In one embodiment, the silicate pollutant treating material comprises sepiolite.
[0006] The process for reducing pollutants from being discharged into the atmosphere comprises disposing an adsorber member in a fluid passageway of the air cleaner assembly, wherein the adsorber member comprises a support comprising a plurality of fluid passageways and a silicate pollutant treating material free from zeolite disposed onto a surface of the support; and contacting a fluid flowing through the fluid passageway with the adsorber member.
[0007] The above-described and other features will be appreciated and understood by those skilled in the art from the following detailed description, drawings, and appended claims.
[0008] Referring now to the figures wherein the like elements are numbered alike:
[0009]
[0010]
[0011]
[0012]
[0013] The present disclosure relates to an air induction system and process for reducing fuel emissions. More particularly, the present disclosure relates to an air induction system and process for eliminating fuel emissions from an air cleaner assembly, for example, eliminating fuel emissions that accumulate in the air cleaner assembly after shutdown of an internal combustion engine.
[0014] Referring now to
[0015] The one or more filter elements for removing particulate matter from an air stream during operation of the internal combustion engine can have an insert or spacer construction that generally includes an outer liner and an inner liner. A media construction can be positioned between the outer liner and inner liner. A variety of materials can be utilized for the outer and inner liners including expanded metal, perforated metal and plastic liners, as examples. In general, the outer and inner liners should preferably: (a) be selected of materials appropriately perforated or otherwise made porous so as not to substantially interfere with airflow through the arrangement; and (b) be of appropriate structural rigidity and strength to contain the media construction and provide the arrangement with sufficient axial strength for the use intended and to protect the media construction from damage. Typical liners have an open area of at least 50%, often 60% or more. Galvanized metal or plastic arrangements are typically preferred. Herein the combination of the outer liner, inner liner and media construction will sometimes be referred to as the media pack. The media construction may comprise a pleated media, or alternatively, a depth media. If pleated media is used, in general, paper or cellulose fiber media or media comprising cellulose fibers and synthetic fibers can be used.
[0016] The filter element may also include first and second opposite end caps. The end caps may comprise a soft, compressible elastomer, such as foamed polyurethane; however, a harder material can be used as one or more of the end caps, with the media and liners secured to the end caps by potting material such as an adhesive, for example, a plastisol adhesive.
[0017] A retainer
[0018] As shown more clearly in
[0019] The second open end
[0020] As previously disclosed, the clamping device
[0021] The retainer
[0022] The adsorber member
[0023] The adsorber member
[0024] Although the substrate can have any size or geometry, the size and geometry are preferably chosen to optimize surface area in the given design parameters. Preferably, the substrate has a honeycomb geometry, with the combs through-channel having any multi-sided or rounded shape, with substantially square, triangular, pentagonal, hexagonal, heptagonal, or octagonal or similar geometries preferred due to ease of manufacturing and increased surface area. Also, although each comb forming the honeycomb may be of a different size, the substrate preferably comprises a honeycomb structure wherein all combs are of about equal size. The substrate may comprise about 60 to about 600 or more fluid passageways (cells) per square inch of cross section. The thickness of the substrate may be about 0.06 inch to about 12 inches with about 0.12 to about 1.0 inches preferred. Preferably the passages are essentially straight from their inlet to their outlet and are defined by walls in which the pollutant treating material may be coated as a washcoat so that the gases flowing through the passages contact the pollutant treating material.
[0025] The pollutant treating material can be capable of adsorbing pollutants contained in the air surrounding the substrate. Although the types of pollutants may vary widely depending on the environmental conditions to which the adsorber member
[0026] In a preferred embodiment, the pollutant treating material comprises silicate materials. The preferred silicate materials are free from zeolites. Suitable silicate materials include, but are not limited to, silicates belonging to the phyllosilicate class of silicates. Phyllosilicates include, but are not limited to, smectites, palygorskites, sepiolites, tuperssuatsiaite, yofortierite, kalifersite, falcondoite, loughlinite, and combinations comprising at least one of the foregoing phyllosilicates, wherein smectites, palygorskites, sepiolites, and combinations comprising at least one of the foregoing phyllosilicates are preferred. In a preferred embodiment, the silicate pollutant treating composition is sepiolite or a composition including sepiolite.
[0027] When loaded onto the support, the silicate loading is preferably about 0.10 g/in
[0028] The silicate material may be either pure, i.e., 100% silicon oxides, or it may comprise other materials, such as, but not limited to, alkaline ions including lithium, sodium, potassium, cesium, magnesium, calcium, strontium, barium and combinations comprising at least one of the foregoing. These alkaline ion silicate materials are preferably prepared by substituting Mg
[0029] The silicate pollutant treating composition may also comprise additional materials. Generally, the additional materials may comprise about 0.01 to about 50 weight percent based on the weight of the total pollutant treating composition. For example, the silicate pollutant treating materials may include catalytic materials of about 0.01 to about 20 weight percent of the silicate pollutant treating composition. Suitable catalysts include active metals such as platinum, palladium, rhodium, iridium, ruthenium, gold and silver, wherein platinum and palladium, and combinations comprising at least one of the foregoing catalysts are preferred. A silver doped magnesium silicate e.g. silver sepiolite is particularly preferred. The silicates may further contain stabilizing metals such as scandium, yttrium, lanthanum, titanium, zirconium, and cerium, wherein zirconium and titanium and combinations comprising at least one of the foregoing are preferred. The silicates may contain metals active for hydrocarbon double bonds such as nickel, copper, and manganese and the like, as well as oxides, alloys, and combinations comprising at least one of the foregoing catalytic materials, wherein nickel and combinations comprising at least one of the foregoing are preferred
[0030] The additional materials, which may form part of the coating, may also include oxides (e.g., alumina, zirconia, titania, and the like), activated carbon, aluminides, and the like, and combinations comprising at least one of the foregoing. Where an aluminide is used, preferably the aluminide comprises an aluminum in combination with at least one additional metal, such as, nickel, iron, titanium, platinum and palladium, and a material to improve oxidation resistance such as barium, strontium, calcium, and magnesium, and oxides, alloys, and combinations comprising at least one of the foregoing, with, titanium, and oxides, alloys, and combinations comprising at least one of the foregoing particularly preferred.
[0031] The pollutant treating materials may also further comprise a binder. A preferred binder is a polymeric binder that can be a thermosetting or thermoplastic polymeric binder. The polymeric binder can have suitable stabilizers and age resistors typical in the polymeric art. The polymer can be a plastic or elastomeric polymer. Most preferred are thermosetting, elastomeric polymers.
[0032] Useful polymeric compositions include polyethylene, polypropylene, polyolefin copolymers, polyisoprene, polybutadiene, polybutadiene copolymers, chlorinated rubber, nitrile rubber, polychloroprene, ethylene-propylene-diene elastomers, polystyrene, polyacrylate, polymethacrylate, polyacrylonitrile, poly(vinyl esters), poly(vinyl halides), polyamides, cellulosic polymers, polyimides, acrylics, vinyl acrylics and styrene acrylics, poly vinyl alcohol, thermoplastic polyesters, thermosetting polyesters, poly(phenylene oxide), poly(phenylene sulfide), fluorinated polymers such as poly(tetrafluoroethylene) polyvinylidene fluoride, poly(vinylfluoride) and chloro/fluoro copolymers such as ethylene chlorotrifluoroethylene copolymer, polyamide, phenolic resins and epoxy resins, polyurethane, and silicone polymers. A most preferred polymeric material is an acrylic polymeric latex.
[0033] An alternate and useful binding material is the use of a zirconium compound. Zirconyl acetate is preferred zirconium compound used. It is believed that zirconia acts as a stabilizer, promotes adsorbtion, promotes hydrocarbon retention, and improves adhesion. Upon calcination, zirconium compounds such as zirconyl acetate are converted to well dispersed nanoparticle of zirconium oxide, which is believed to be the binding material. Various useful zirconium compounds include zirconium acetates, zirconium citrates, zirconium formates, zirconium ethoxides, zirconium methoxides, zirconium propoxides, zirconium hydroxides, and the like. for generating discrete dispersions of zirconium oxide.
[0034] A suitable application of the retainer 26 described herein is for use as an air cleaner/air meter connector (“connector”). The air meter
[0035] Although the heating elements, sensing elements, interconnect traces, and bonding pads are preferably formed out of a single metal layer such as platinum, it is not necessary that they all be the same material. However, the heating elements are preferably made of a material with a high temperature coefficient of resistance, such as platinum, gold, silver, or combinations comprising at least one of the foregoing to allow a temperature difference to result in a resistance differential between the two heating elements in the presence of airflow.
[0036] A passivation layer may also be deposited on the topside of the air meter. Such a passivation layer helps to prevent contaminants from interfering with the functioning of the heating elements and sensing element.
[0037] During engine operation, the air cleaner assembly
[0038] Advantageously, the air cleaner assembly
[0039] The disclosure is further illustrated by the following non-limiting examples.
[0040] In this example, sepiolite obtained from IMV Nevada, Amardosa Valley, Nev., was calcined at 500° C. for about 4 hours. The calcined sepiolite was milled and screened through 325 mesh screen. A slurry in acetone was made consisting of 81 wt % sepiolite, 9 wt % polyacrylonitrile, and 10 wt % N-methylpyrolidinone. The slurry was made about 60 weight percent solids. The slurry was ball milled for about 2 hours. The milled slurry was then passed over an expanded aluminum honeycomb substrate with hexagonal cells about 0.0625 inches in diameter, 256 cells per cubic inch. The coated honeycomb substrate was then heated to about 150° C. to evaporate the N-methylpyrolidinone and acetone. The heating exposed the porosity of the coating. The coating had a thickness of about 20 to about 40 microns.
[0041] In this example, an expanded aluminum honeycomb substrate was coated with sepiolite as in Example 1. The coated honeycomb substrate was heated to about 350° C. to decompose the zirconium citrate. The coating had a thickness of about 40 to about 60 microns.
[0042] In this example, about 740.1 grams silica was mixed with 69.1 grams magnesium acetate from Aldrich. The mixture was calcined to 738° C. for about 9 hours. The calcined mixture was ball milled for about 4 hours then screened through 325 mesh screen. The resulting mixture is a synthetic sepiolite. A slurry was made consisting of 89 wt % synthetic sepiolite and 11 wt % zirconium citrate. Water was added to make a slurry of about 46 weight percent solids. The slurry was ball milled for about 2 hours. The milled slurry was passed over expanded aluminum honeycomb substrate with hexagonal cells about 0.125 inches in diameter, 64 cells per cubic inch. The coated honeycomb substrate was heated to about 350° C. to decompose the zirconium citrate. The substrate was post impregnated with a silver acetate solution. The resulting adsorption material layer disposed upon the catalyst washcoat layer comprised about 1.0 wt % silver oxide by weight of the adsorption material layer. The silver sepiolite coating had a thickness of about 40 to about 60 microns.
[0043] In this example, a slurry was made consisting of 500 grams synthetic sepiolite prepared as in Example 3, 50 grams dibutyl phthalate and 50 grams poly(vinylidenedifluoride) powder. Acetone was added to make the slurry about 46 weight percent solids. The slurry was ball milled for 2 hours. The milled slurry was passed over expanded aluminum honeycomb substrate with hexagonal cells about 0.125 inches in diameter, 64 cells per cubic inch. The coated honeycomb substrate was heated to about 280° C. The sepiolite coating had a thickness of about 40 to about 60 microns.
[0044] In this example, the synthetic sepiolite prepared as in Example 3 was ion exchanged with a silver trifluoroacetate solution. The silver trifluoroacetate-sepiolite was then calcined at 400° C. A 1.0 wt % silver doped sepiolite was recovered. A slurry was made consisting of 500 grams silver doped synthetic sepiolite, 50 grams dibutyl phthalate, 50 grams poly(vinylidenedifluoride) powder as binder. Acetone was added to make the slurry about 46 weight percent solids. The slurry was ball milled for 2 hours. The milled slurry was passed over expanded aluminum honeycomb substrate with hexagonal cells about 0.125 inches in diameter, 64 cells per cubic inch. The coated honeycomb substrate was heated to about 280° C. The silver sepiolite coating had a thickness of about 40 to about 60 microns.
[0045] While the disclosure has been described with reference to an exemplary embodiment, it will be understood by those skilled in the art that various changes may be made and equivalents may be substituted for elements thereof without departing from the scope of the disclosure. In addition, many modifications may be made to adapt a particular situation or material to the teachings of the disclosure without departing from the essential scope thereof. Therefore, it is intended that the disclosure not be limited to the particular embodiment disclosed as the best mode contemplated for carrying out this disclosure, but that the disclosure will include all embodiments falling within the scope of the appended claims.