The invention concerns a procedure and a control unit according to the preambles of the independent claims.
Such a procedure and such a control unit are each respectively known from the German patent DE 103 23 607 A1. This text shows in
A particle filter has a structure with a multiplicity of canals, which alternately are so closed that the particle laden exhaust gas has to stream through porous walls of the honeycomb body. In so doing, the particles are deposited in the pores. Depending upon the porosity of the ceramic honeycomb body, the degree of effectiveness of the filter fluctuates between 70 and 90%. In order to avoid an inadmissibly high exhaust gas back pressure due to particle residues, the particle filter must be regenerated.
An SCR-catalytic converter facilitates a selective catalytic reduction of nitrogen oxides to molecular nitrogen, whereby ammonia serves as the reducing agent, which in a known manner can be derived from a urea-water-solution in a hydrolysis catalytic converter connected upstream from the SCR-catalytic converter. The conversion of the urea-water-solution can also take place at the SCR-catalytic converter, so that a separate hydrolysis catalytic converter must not necessarily be present.
The “selective catalytic reaction” is described in connection with the construction of a SCR-catalytic converter in D. Schoeppe et al., “A closed-loop controlled exhaust gas aftertreatment system to meet future emission limits for diesel motors”, progress reports, VDI, file 12, number 267, volume 1 (1996), 17th international Viennese motor symposium, pages 332-353. The SCR-catalytic converter converts a reducing agent into ammonia (NH3), with which the nitrogen oxides are selectively and catalytically converted to nitrogen and water.
In the integrated SCR/DPF-system known from the German patent DE 103 23 607 the structure of the particle filter contains SCR-active catalytic centers. In order to guarantee the desired particle reduction in an enduring and reliable manner, the soot collected in the particle filter should be removed from time to time. This occurs as a rule by means of a combustion of the sooty particles at an elevated particle filter temperature, which is also called thermal regeneration. In a vehicle with a diesel motor and a particle filter, such a thermal regeneration is typically set off after driving several hundred kilometers by an elevation of the exhaust gas temperature. The exhaust gas temperature can, for example, thereby be set off by selective degradations of the efficiency of the engine's combustion.
During such regenerations of an integrated SCR/DPF-system, offensive odors occur.
With regard to this background information, the task of the invention is the description of a procedure and of a control unit of the kind mentioned at the beginning of the application, which allows a regeneration of an integrated SCR/DPF-system without the occurrence of offensive odors.
This task is solved with a procedure and a control unit of the kind mentioned at the beginning of the application in each case by means of the distinguishing characteristics of the accompanying independent claim. It was recognized during an analysis of the odor problem that the offensive odors were set off by a release of ammonia, which occurred during an increase in the system temperature. By way of the decrease in the supply of the reducing agent before the thermal regeneration, consumed ammonia is no longer or to a decreased extent replaced at the SCR active catalytic substances. During a thermal regeneration of the particle filter, only a small amount or no ammonia is then released.
It is thus preferred that the supply of the reducing agent is reduced already before the thermal regeneration. In so doing, stored ammonia is consumed at the catalytic centers by means of the continuing SCR-reaction, before it can come to a desorption of ammonia, which is thermally contingent.
It is also preferred that a stored mass of ammonia in the particle filter is reduced from an initial value of the mass to a second value of the mass, before the particle filter reaches a temperature at which the stored up soot combusts. The second value of the mass corresponds thereby preferably to a lower ammonia level standard, at which no significant amounts of ammonia can be desorbed even at an elevated temperature. Thus, a released amount of ammonia is then no longer significant, if its odor under normal conditions cannot be noticed.
It is additionally preferable in order to avoid offensive smells that the supply of the reducing agent also remains reduced during the thermal regeneration.
Provision is made in an additional preferred embodiment for the supply of the reducing agent to be again elevated after a thermal regeneration. The nitrogen oxide conversion capability is interfered with by the reduced supply of the reducing agent. The elevation of the supply of the reducing agent again removes the interference. The nitrogen oxide emissions are thereby only temporarily interfered with during the relatively seldom occurring thermal regeneration. The duration of the interference can thereby be shortened, in that the elevation of the supply of the reducing agent occurs in such a way at the beginning, that an ammonia storage area of the integrated SCR/DPF-system is filled again quickly. This can occur by means of a short term excessive supply of the reducing agent.
In order to further reduce the interference of a nitrogen oxide conversion and in order to minimize the increased fuel consumption, which is connected with a thermal regeneration of the integrated SCR/DPF-system, the beginning of a regeneration is preferably controlled as a function of a measurement for a flow resistance of the particle filter. If the measurement for the flow resistance exceeds a threshold value, a thermal regeneration is set off or the triggering is prepared. Such a demand justified triggering results preferably due to the fact, that the measurement is ascertained from the signal of a pressure differential sensor, which ascertains a difference in pressures in front of and behind the particle filter. Alternatively or additionally the measurement for the flow resistance can, however, also be formed as a function of the operating parameters of the particle filter by means of a computer model.
Additional advantages result from the description and the figures provided.
It is understood, that the previously stated characteristics and the subsequent characteristics yet to be explained are not only applicable in the combination given in each case, but also in other combinations individually without departing from the scope of the invention at hand.
Examples of embodiment of the invention are depicted in the drawings and are explained in detail in the following description. The following are shown respectively schematically:
For the purpose of exhaust gas purification, the known emission control system 12 of
The integrated SCR/DPF-module 20 has a structure 22, in which alternately closed canals are so designed, that the canals, which are open facing the entrance of the SCR/DPF module, and are closed facing the opposing exit and vice versa. The exhaust gas of the internal combustion engine 10 must, therefore, in the emission control system according to
The integrated SCR/DPF-module 20 is so constituted, that exhaust gas passing through it comes in contact with catalytic centers. In so doing, materials of the catalytic centers are so selected, that a SCR-capability results. This capability can, for example, be produced in such a manner, that the surface areas of the alternately closed canals of the structure 22 are covered with a gas permeable catalytic layer. The structure 22 serves in this case as a supporting structure for the SCR-active coating as well as a particle filter, in which the sooty particles are eliminated. Alternatively and/or additionally, the catalytic layer can also be located in the porous walls of the canals.
The catalytic coating of the canals and/or the pores of the structure 22 of the SCR/DPF-module 20 facilitates a selective catalytic reduction of nitrogen oxides to molecular nitrogen, whereby ammonia serves as the reducing agent. The reducing agent ammonia is derived in one embodiment by means of a hydrolytic reaction in the SCR/DPF module 20 from a urea-water-solution, which is metered from a reducing agent metering system 24 to the exhaust gas in front of the SCR/DPF-module 20 or the structure 22. The reducing agent metering system 24 has essentially a reducing agent tank 26, a metering valve 28 and a jet 30. The metering valve 28 is controlled as a function of operating parameters of the internal combustion engine 10 by the control unit 18. It is, however, understood, that the invention is not dependent upon a specific kind of production of the reducing agent.
In this context especially the temperature T of the emission control system 12 or one of its components belongs to the operating parameters of the internal combustion engine 10. For the acquisition of the temperature T, provision is made in
With an increasing mass of deposited sooty particles, the flow resistance of the SCR/DPF-module increases and with that the exhaust gas back pressure. In order to avoid an inadmissibly high exhaust gas back pressure due to particle residue, the SCR/DPF-module must be regenerated.
In the embodiment of
The curve 36 shows the progression of the pressure differential values dp at a certain value of the exhaust gas mass stream, while the curve 38 shows the progression of a temperature of the SCR/DPF-module. In this context it must be expressly pointed out, that the depiction of
The loading of the SCRIDPF-module 20 with soot on the other hand increases possibly over a distance of several hundred kilometers and at the same time over several hours of operation before a thermal regeneration is set off. The increase in the pressure differential (dp) (curve 36), in which an increased loading of the SCR/DPF-module with soot is displayed, is for reasons of clarity is more steeply depicted than is to be expected in actual systems.
The SCR/DPF-module 20 first filters sooty particles out of the exhaust gas of the internal combustion engine 10. Chronologically parallel to that, nitrogen oxides in the exhaust gas of the internal combustion engine 10 are reduced in the SCR/DPF-module 20 to molecular nitrogen. In order to maintain the selective catalytic reaction, a reducing agent is at first continually added to the exhaust gas. The metering of the reducing agent occurs by way of the valve 28 and the jet 30 in
At the point in time 11 a measurement for a flow resistance of the SCR_DPF-module 20 reaches a threshold value. The measurement can be formed from the signal dp of the pressure differential sensor 34 and/or as a function of the operating parameters of the SCR/DPF-module 20 and/or of the internal combustion engine 10 using a computer model. The control unit 18 registers the fact that the threshold value has been exceeded and sets off a thermal regeneration of the SCR/DPF-module 20 by way of an elevation of the exhaust gas temperature T at the entrance of the SCR/DPF-module 20. The time duration of the increase in temperature determines the time duration tR of the regeneration. Furthermore, the control unit 18 reduces the supply of the reducing agent during the thermal regeneration. Ammonia stored in the SCR/DPF-module 20 and consumed during the selective catalytic reduction is for this reason temporarily no longer replaced by an additional delivery of the reducing agent. The amount of released ammonia is thereby reduced, which is not consumed during the nitrogen oxide reduction and that can escape behind the SCR/DPF-module 20 and cause offensive odors.
In a preferred embodiment the supply of the reducing agent is already reduced before the thermal regeneration. When the threshold value is exceeded by the measurement for the flow resistance, a preparation of the thermal regeneration initially is set off. The actual thermal regeneration is then delayed in being set off.
Thus the ammonia stored in the SCR-DPF-module is consumed for the reduction of the nitrogen oxides, before the increase in temperature is set off. In the depiction of
Subsequently the supply of the reducing agent also remains decreased during the thermal regeneration. In so doing, the decrease can go as far as a complete interruption of the supply of the reducing agent. It is, however, preferable, that a marginal reducing agent flow be maintained. In the process the nitrate monoxide resulting from the conversion of the precipitated carbon during the thermal regeneration can be converted to molecular nitrogen and water. Beside the nitrate monoxide resulting from the conversion of the carbon, nitrogen oxide emitted from the internal combustion engine 10 is, of course, converted by means of the selective catalytic reaction in the porous catalytic structure 82.
After a thermal regeneration, which ends at the point in time t3, the supply of the reducing agent is again increased, in order to again increase the nitrogen oxide reduction. At the same time the supply of the regeneration agent can also be increased excessively for a short time above the required dosage for steady state conditions in order to rapidly fill the ammonia storage of the SCR/DPF-module. This is depicted in
Number | Date | Country | Kind |
---|---|---|---|
10 2005 061 873.1 | Dec 2005 | DE | national |