The present invention relates generally to engine exhaust treatment systems. More particularly, the present disclosure relates to engine exhaust treatment systems including diesel particulate filters and heaters for regenerating the diesel particulate filters.
Vehicles equipped with diesel engines may include exhaust systems that have diesel particulate filters for removing particulate matter from the exhaust stream. With use, soot or other carbon-based particulate matter accumulates on the diesel particulate filters. As particulate matter accumulates on the diesel particulate filters, the restriction of the filters increases causing the buildup of undesirable back pressure in the exhaust systems. High back pressures decrease engine efficiency. Therefore, to prevent diesel particulate filters from becoming excessively loaded, diesel particulate filters should be regularly regenerated by burning off (i.e., oxidizing) the particulates that accumulate on the filters. Since the particulate matter captured by diesel particulate filters is mainly carbon and hydrocarbons, its chemical energy is high. Once ignited, the particulate matter burns and releases a relatively large amount of heat.
Systems have been proposed for regenerating diesel particulate filters. Some systems use a fuel fed burner positioned upstream of a diesel particulate filter to cause regeneration (see U.S. Pat. No. 4,167,852). Other systems use an electric heater to regenerate a diesel particulate filter (see U.S. Pat. Nos. 4,270,936; 4,276,066; 4,319,896; 4,851,015; 4,899,540; 5,388,400 and British Published Application No. 2,134,407). Detuning techniques are also used to regenerate diesel particulate filters by raising the temperature of exhaust gas at selected times (see U.S. Pat. Nos. 4,211,075 and 3,499,260). Self regeneration systems have also been proposed. Self regeneration systems can use a catalyst on the substrate of the diesel particulate filter to lower the ignition temperature of the particulate matter captured on the filter. An example of a self regeneration system is disclosed in U.S. Pat. No. 4,902,487.
One aspect of the present disclosure relates to an exhaust treatment device including a diesel particulate filter (DPF), a diesel oxidation catalyst (DOC) (i.e., a catalytic converter) and an electric heater for regenerating the DPF. In certain embodiments, the heater is positioned between the DPF and the DOC.
Another aspect of the disclosure relates to a shore station for providing power and combustion air to an exhaust treatment device equipped with an electric heater.
Examples representative of a variety of inventive aspects are set forth in the description that follows. The inventive aspects relate to individual features as well as combinations of features. It is to be understood that both the forgoing general description and the following detailed description merely provide examples of how the inventive aspects may be put into practice, and are not intended to limit the broad spirit and scope of the inventive aspects.
While the invention is amenable to various modifications and alternative forms, specifics thereof have been shown by way of example in the drawings and will be described in detail below. It is to be understood, however, that the intention is not to limit the invention to the particular embodiments described. On the contrary, the invention is intended to cover all modifications, equivalents, and alternatives falling within the scope of the disclosure.
The outer body 22 of the exhaust treatment device 20 includes a cylindrical conduit structure 44 that extends from the inlet end 24 to the outlet end 26 of the outer body 22. The cylindrical conduit structure 44 includes a first section 46, a second section 48, a third section 50, a fourth section 52, and a fifth section 54. The first and fifth sections 46, 54 respectively define the inlet and outlet ends 24, 26 of the outer body 22. The second section 48 houses the DOC 28, the third section 50 houses the heater 32 and the fourth section 52 houses the DPF 30. Mechanical connection interfaces 56 are provided between the first and second sections 46, 48, between the second and third sections 48, 50, between the third and fourth sections 50, 52 and between the fourth and fifth sections 52, 54. The mechanical connection interfaces 56 are adapted to allow the various sections to be disconnected from one another to allow access to the interior of the outer body 22. In the depicted embodiment, mechanical connection interfaces 56 include joints 57 at which the sections are connected together. The sections include flanges 58 positioned at the joints. The flanges 58 are secured together by clamps such as V-band clamps 30 that prevent the sections from unintentionally separating at the joints 57. To facilitate assembly, selected sections can include pilot portions that fit into adjacent sections at the joints.
Referring to
The inlet pipe 64 also defines first and second sets of openings, 74, 76 that extend radially through the inlet pipe 64. The first set of openings 74 is adapted to direct exhaust flow radially outwardly from the inlet pipe 64. The first set of openings 74 cooperate with the flow dispersion plug 70 to provide flow uniformity at the upstream face of the DOC 28. The second set of openings 76 provide fluid communication between the interior of the inlet pipe 64 and a resonating chamber 78 (e.g., an expansion chamber). The resonating chamber 78 provides sound muffling within the exhaust treatment device 20. As depicted at
Referring still to
As depicted at
Referring to
Referring back to
The DOC 28 of the exhaust treatment device 20 is used to convert carbon monoxide and hydrocarbons in the exhaust stream into carbon dioxide and water. As shown at
Referring still to
The particulate mass reduction efficiency of the DOC is dependent upon the concentration of particulate material in the exhaust stream being treated. Post 1993 on-road diesel engines (e.g., four stroke 150-600 horsepower) typically have particulate matter levels of 0.10 grams/brake horsepower hour (bhp-hr) or better. For treating the exhaust stream of such engines, the DOC may have a particulate mass reduction efficiency of 25% or less. In other embodiments, the DOC may have a particulate mass reduction efficiency of 20% or less. For earlier model engines having higher PM emission rates, the DOC may achieve particulate mass reduction efficiencies as high as 50 percent.
For the purposes of this specification, particulate mass reduction efficiency is determined by subtracting the particulate mass that enters the DOC from the particulate mass that exits the DOC, and by dividing the difference by the particulate mass that enters the DOC. The test duration and engine cycling during testing are preferably determined by the federal test procedure (FTP) heavy-duty transient cycle that is currently used for emission testing of heavy-duty on-road engines in the United States (see C.F.R. Tile 40, Part 86.1333). Carbon monoxide and other contaminants can also be oxidized within the DOC.
It will be appreciated that unlike filters which rely primarily on mechanically capturing particulate material within a filter media, catalytic converters rely on catalyzed oxidation to remove particulate material from an exhaust stream. Therefore, catalytic converters are typically adapted to resist particulate loading. For example, a typical catalytic converter substrate has passages that extend completely from the upstream end of the substrate to the downstream end of the substrate. In this way, flow is not forced through the walls of the substrate. The channels are preferably large enough in cross-sectional area to prevent particulate material from accumulating on the substrate.
Suitable catalytic converter substrates can have a variety of other configurations. Example catalytic converter configurations having both corrugated metal and porous ceramic substrates/cores are described in U.S. Pat. No. 5,355,973, that is hereby incorporated by reference in its entirety. In certain embodiments, the DOC can be sized such that in use, the catalytic converter has a space velocity (volume metric flow rate through the DOC divided by the volume of the DOC) less than 150,000 per hour or in the range of 50,000 to 150,000 per hour. In one example embodiment, the DOC substrate can have a cell density of at least 200 cells per square inch, or in the range of 200 to 400 cells per square inch. Exemplary materials for manufacturing the DOC substrate include cordierite, mullite, alumina, SiC, refractory metal oxides, or other materials conventionally used as substrate.
The substrate 130 preferably includes a catalyst. For example, the substrate 130 can be made of a catalyst, impregnated with a catalyst or coated with a catalyst. Example catalysts include precious metals such as platinum, palladium and rhodium. In a preferred embodiment, the DOC substrate is lightly catalyzed with a precious metal catalyst. For example, in one embodiment, the DOC substrate has a precious metal loading (e.g., a platinum loading) of 15 grams or less per cubic foot. In another embodiment, the DOC substrate has a precious metal loading (e.g., a platinum loading) equal to or less than 10 grams per cubic feet or equal to or less than 5 grams per cubic foot. By lightly catalyzing the DOC substrate, the amount of NO2 generated at the DOC substrate during treatment of exhaust is minimal. The catalysts can also include other types of materials such as alumina, cerium oxide, base metal oxides (e.g., lanthanum, vanadium, etc.) or zeolites. Rare earth metal oxides can also be used as catalysts.
The DOC 20 is preferably positioned relatively close to the resistive heating element 92. For example, in one embodiment, the downstream face of the DOC is spaced a distance ranging from 1 to 4 inches from the upstream face of the resistive heating element 92. During regeneration, the DOC functions to store heat thereby heating the combustion air that flows to the DPF. Additionally, the DOC functions to reflect heat back towards the DPF. Moreover, the DOC assists in providing a dry soot pack at the DPF thereby facilitating the regeneration process.
Referring back to
As shown at
Still referring to
In alternative embodiments, the diesel particulate filter can have a configuration similar to the diesel particulate filter disclosed in U.S. Pat. No. 4,851,015 that is hereby incorporated by reference in its entirety. Example materials for manufacturing the DPF substrate include cordierite, mullite, alumina, SiC, refractory metal oxides or other materials conventionally used at DPF substrates.
It is preferred for the DPF to be lightly catalyzed or to not be catalyzed at all. In a preferred embodiment, the DPF has a precious metal loading that is less than the precious metal loading of the DOC. By minimizing the precious metal loading on the DPF, the production of NO2 during treatment of exhaust is minimized.
The DPF 30 preferably has a particulate mass reduction efficiency greater than 75%. More preferably, the DPF 30 has a particulate mass reduction efficiency greater than 85%. Most preferably, the DPF 30 has a particulate mass reduction efficiency equal to or greater than 90%. For the purposes of this specification, particulate mass reduction efficiency is determined by subtracting the particulate mass that enters the DPF from the particulate mass that exits the DPF, and by dividing the difference by the particulate mass that enters the DPF. The test duration and engine cycling during testing are preferably determined by the federal test procedure (FTP) heavy-duty transient cycle that is currently used for emission testing of heavy-duty on-road engines in the United States (see C.F.R. Tile 40, Part 86.1333).
To facilitate regeneration, it is preferred for the DPF to have a relatively low concentration of cells per square inch. For example, in one embodiment, the DPF has less than or equal to 150 cells per square inch. In another embodiment, the DPF has less than or equal to 100 cells per square inch. In a preferred embodiment, the DPF has approximately 90 cells per square inch. By using a relatively low concentration of cells within the DPF substrate, it is possible for the substrate walls 170 defining the passages 172 to be relatively thick so that the walls are less prone to cracking. In one embodiment, the walls 170 have a thickness of in the range of 0.010-030 inches.
It is desired for the device 20 to not cause substantial increases in the amount of NO2 within the exhaust stream. In a preferred embodiment, the ratio of NO2 to NOx in the exhaust gas downstream from the exhaust treatment system is no more than 20 percent greater than the ratio of NO2 to NOx in the exhaust gas upstream from the exhaust treatment system. In other words, if the engine-out NOx mass flow rate is (NOx)eng, the engine-out NO2 mass flow rate is (NO2)eng, and the exhaust-treatment-system-out NO2 mass flow rate is (NO2)sys, then the ratio
is less than 0.20. In other embodiments, the ratio is less than 0.1 or less than 0.05.
In still other embodiments, the ratio of NO2 to NOx in the exhaust gas between the DOC and the DPF is no more than 20 percent greater than the ratio of NO2 to NOx in the exhaust gas upstream from the DOC. In other embodiments, the ratio of NO2 to NOx in the exhaust gas between the DOC and the DPF is no more than 10 percent greater or no more than 5 percent greater than the ratio of NO2 to NOx in the exhaust gas upstream from the DOC.
The back pressure sensor 38 of the exhaust treatment device 20 measures the back pressure generated behind the DPF 30. In certain embodiments, the back pressure monitor interfaces with an indicator provided in the cab of the vehicle on which the exhaust treatment device 20 is installed. When the back pressure exceeds a predetermined amount, the indicator (e.g., a light) provides an indication to the driver that the exhaust treatment device is in need of regeneration.
It will be appreciated that power and combustion air for the exhaust treatment device can be provided from either an onboard source or an offboard source. For example, vehicles may be equipped with onboard generators, controllers and sources of compressed air to provide onboard power, air and regeneration control to the exhaust treatment device 20. Alternatively, an offboard station can be used to provide power, regeneration control and combustion air to the exhaust treatment device. Offboard stations are particularly suitable for use in regenerating exhaust treatment devices installed on domiciled fleets (e.g., buses) that are periodically parked (e.g., nightly) at a given location. In still other embodiments, regeneration control may be provided onboard, while air and power are provided offboard.
The control unit is preferably equipped with a control panel. An example control panel is shown at
The control unit 202 also controls the power provided to the exhaust treatment devices 20 being regenerated. For example, the control unit 202 includes switches 312 that interface with the controller 306. The switches 312 allow the controller 306 to selectively start or stop power from being supplied to the heating elements of the exhaust treatment devices 20. Temperature controllers 314 also assist in controlling operation of the heating elements of the exhaust treatment devices 20. The temperature controllers 314 receive temperature feedback from the thermocouples of the exhaust treatment devices 20. The temperature controllers 314 interface with switches 316 (e.g., silicon control rectifiers) that control the power provided to the heating elements. The temperature controllers 314 can be programmed to control the switches 316 so that the heating elements of the exhaust treatment devices 20 are heated to a desired temperature. The temperature controllers 314 can include displays for displaying the set/desired regeneration temperature, and also for displaying the actual temperature of the heating element as indicated from data provided by the thermocouple. The temperature controllers 314 interface with the controller 306 to provide feedback regarding the temperature of the heating elements. In the event that the heating elements heat too slowly or become overheated, the controller will discontinue the regeneration process by actuating the switches 312 so that no additional power is provided to the heating element.
When multiple exhaust treatment devices 20 are being regenerated, the controller will alternately open and close the switches 312 so that power alternates between the heating elements of the exhaust treatment devices.
In use of the shore station 200, the regeneration cord 220 is plugged into the bulkhead 304 of a vehicle 300. By plugging the regeneration cord 220 into the bulkhead 304, the shore station 200 can provide power and air to the exhaust treatment devices 20 during regeneration, can monitor the temperature of the heating elements, and can control the regeneration process. To start the regeneration process, the start button 230 is depressed causing power to be provided to the heating element. Concurrently, light 234 is illuminated. During the regeneration process, the power to the heating element can be stopped at any time by manually depressing the emergency stop button 232.
If after three minutes the temperature controller 314 is not sensing 500° F. at the heating element, the controller 306 aborts the start up process and the light 234 is flashed indicating a regeneration failure. Similarly, if at any time the temperature controller 314 senses a temperature over 1400° F. at the heating element, the controller 306 aborts the regeneration cycle and the light 234 is flashed.
Under normal operating conditions, the controller will control an initial 20 minute warm up sequence. During the warm up sequence, no compressed air is provided to the exhaust treatment device. After the 20 minute warm up, the controller 306 begins opening and closing the solenoid 308 to provide pulses of air to the exhaust treatment device. In one embodiment, the air is pulsed at a rate of 1 second on and 15 seconds off. This generates an air flow rate of at least about 3 cubic feet per minute, and preferably at least about 4 cubic feet per minute. During this sequence, the light 234 continues to be illuminated. Additionally, if during the regeneration sequence, the pressure provided by the air line 212 falls below a predetermined level, the controller 306 will abort the sequence.
After a predetermined time period (e.g., 4 hours and 20 minutes), the controller 306 stops the regeneration process and begins the cool down process. To begin the cool down process, power to the heating element is terminated. Also, the amount of air provided to the exhaust treatment device 20 can be increased. For example, air can be provided at a pulse rate of 1 second on and 6 seconds off. During cool down, the light 234 is turned off and the light 236 is turned on.
After about 7 hours from initiating the regeneration sequence, the solenoid 308 is de-energized and the cool down cycle ends. The light 237 is then flashed indicating that the entire cycle is complete.
Further information concerning regeneration cycles and recipes can be found in PCT Patent Application No. PCT/US2006/001850, filed on Jan. 18, 2006 and entitled Apparatus for Combusting Collected Diesel Exhaust Material from Aftertreatment Devices and Methods that is hereby incorporated by reference in its entirety.
The above specification, examples and data provide a complete description of the manufacture and use of the composition of the invention. Since many embodiments of the invention can be made without departing from the spirit and scope of the invention, the invention resides in the claims hereinafter appended.
This application is a continuation of application Ser. No. 11/753,986, filed May 25, 2007, now U.S. Pat. No. 8,117,832, Issued Feb. 21, 2012, which application claims the benefit of provisional application Ser. No. 60/814,952, filed Jun. 19, 2006, which applications are incorporated herein by reference in their entirety.
Number | Name | Date | Kind |
---|---|---|---|
3499260 | Forman | Mar 1970 | A |
4167852 | Ludecke | Sep 1979 | A |
4211075 | Ludecke et al. | Jul 1980 | A |
4270936 | Mann | Jun 1981 | A |
4276066 | Bly et al. | Jun 1981 | A |
4319896 | Sweeney | Mar 1982 | A |
4395269 | Schuler | Jul 1983 | A |
4452616 | Gillingham et al. | Jun 1984 | A |
4456457 | Nozawa et al. | Jun 1984 | A |
4504293 | Gillingham et al. | Mar 1985 | A |
4505106 | Frankenberg et al. | Mar 1985 | A |
4573317 | Ludecke | Mar 1986 | A |
4686827 | Wade et al. | Aug 1987 | A |
4735639 | Johnstone | Apr 1988 | A |
4851015 | Wagner et al. | Jul 1989 | A |
4867768 | Wagner et al. | Sep 1989 | A |
4878928 | Wagner et al. | Nov 1989 | A |
4899540 | Wagner et al. | Feb 1990 | A |
4902309 | Hempenstall | Feb 1990 | A |
4902487 | Cooper et al. | Feb 1990 | A |
5042249 | Erdmannsdoerfer | Aug 1991 | A |
5053603 | Wagner et al. | Oct 1991 | A |
5065574 | Bailey | Nov 1991 | A |
5101095 | Wagner et al. | Mar 1992 | A |
5203166 | Miller | Apr 1993 | A |
5224973 | Hoppenstedt et al. | Jul 1993 | A |
5355973 | Wagner et al. | Oct 1994 | A |
5388400 | Hoppenstedt et al. | Feb 1995 | A |
5397550 | Marino, Jr. | Mar 1995 | A |
5400590 | Wagner et al. | Mar 1995 | A |
5435129 | Hosoya et al. | Jul 1995 | A |
5458673 | Kojima et al. | Oct 1995 | A |
5551971 | Chadderton et al. | Sep 1996 | A |
5833725 | Dehn et al. | Nov 1998 | A |
5930994 | Shimato et al. | Aug 1999 | A |
6090172 | Dementhon et al. | Jul 2000 | A |
6233926 | Bailey et al. | May 2001 | B1 |
6641646 | Rosenberg | Nov 2003 | B2 |
6922891 | Marino, Jr. | Aug 2005 | B1 |
7357829 | Ehlers | Apr 2008 | B2 |
7384455 | Sellers et al. | Jun 2008 | B2 |
7410521 | Sellers et al. | Aug 2008 | B2 |
7410529 | Sellers et al. | Aug 2008 | B2 |
7419532 | Sellers et al. | Sep 2008 | B2 |
7421839 | Igarashi | Sep 2008 | B2 |
7458207 | Ehlers | Dec 2008 | B2 |
7462222 | Sellers et al. | Dec 2008 | B2 |
7563309 | Simpson, Jr. | Jul 2009 | B2 |
7582141 | Ehlers | Sep 2009 | B2 |
7648792 | Kaschmitter et al. | Jan 2010 | B2 |
7716922 | Ehlers | May 2010 | B2 |
7951346 | Girdlestone et al. | May 2011 | B2 |
8117832 | Wagner et al. | Feb 2012 | B2 |
8142552 | Meister et al. | Mar 2012 | B2 |
8157897 | Meister et al. | Apr 2012 | B2 |
8172339 | Fries et al. | May 2012 | B2 |
8256060 | Wagner et al. | Sep 2012 | B2 |
20040226287 | Edgar et al. | Nov 2004 | A1 |
20050153828 | Uekusa et al. | Jul 2005 | A1 |
20050160724 | Valentine et al. | Jul 2005 | A1 |
20050247051 | Wagner et al. | Nov 2005 | A1 |
20060070360 | Sellers et al. | Apr 2006 | A1 |
20060120936 | Alive et al. | Jun 2006 | A1 |
20060137329 | Lowe et al. | Jun 2006 | A1 |
20060168952 | Opris | Aug 2006 | A1 |
20060191412 | Sellers et al. | Aug 2006 | A1 |
20090044523 | Wagner et al. | Feb 2009 | A1 |
Number | Date | Country |
---|---|---|
2134407 | Aug 1984 | GB |
2002097931 | Apr 2002 | JP |
2003027922 | Jan 2003 | JP |
2004239072 | Aug 2004 | JP |
WO 9303262 | Feb 1993 | WO |
WO 9523280 | Aug 1995 | WO |
WO 2005028824 | Mar 2005 | WO |
WO 2006096244 | Sep 2006 | WO |
Entry |
---|
Cleaire Products Catalog, Horizon™, May 10, 2006, 7 Pages. |
Engine Control Systems, “CombiClean™—the diesel particulate filter cleaning station for all your filter cleaning needs,” Jan. 2006, 3 Pages. |
Kilcarr, Sean, “Truck Engine Emissions Update: The Road to '07”, Dec. 1, 2004, archived Feb. 15, 2005, Waste Age, pp. 1-4. |
Kojima, English Abstract of JP 2003-027922 A, Jan. 29, 2003. |
Kojima, Machine Translation of JP 2003-027922 A, Jan. 29, 2003. |
Number | Date | Country | |
---|---|---|---|
20120291895 A1 | Nov 2012 | US |
Number | Date | Country | |
---|---|---|---|
60814952 | Jun 2006 | US |
Number | Date | Country | |
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Parent | 11753986 | May 2007 | US |
Child | 13401417 | US |