Patent Grant
10392997
This application claims priority to and the benefit of DE 102016221272.9 filed on Oct. 28, 2016. The disclosure of the above application is incorporated herein by reference.
The present disclosure relates to a method for operating an exhaust gas aftertreatment device for cleaning an exhaust gas flow of a motor vehicle with an internal combustion engine operated with oxygen surplus in normal mode. The present disclosure furthermore concerns an exhaust gas aftertreatment device and a motor vehicle with such an exhaust gas aftertreatment device.
The statements in this section merely provide background information related to the present disclosure and may not constitute prior art.
Exhaust gas aftertreatment devices clean combustion gases after they have left the combustion chamber of an internal combustion engine driving the motor vehicle, using a mechanical, catalytic or chemical method, in order to comply with the legal pollutant limits.
Diesel engines and modern lean-mix petrol engines work in lean mode, i.e. with an oxygen surplus (λ>1). Conventional three-way catalysts cannot therefore be used. The oxidation of CO (carbon monoxide) and CmHn (incompletely burned hydrocarbons) is still possible with oxygen surplus, in a similar manner to a conventional three-way catalyst, but the NOx (nitrous oxide) must be temporarily stored. The catalytic reduction thereof takes place cyclically with a stoichiometric to rich exhaust gas mixture. Therefore, catalysts with additional chemical elements are required which allow storage of NOx, known as NOx storage catalysts.
In order to achieve this temporary storage of nitrous oxides in the NOx storage catalyst, a noble metal catalyst such as platinum, and an NOx storage component which is usually an earth alkali metal such as barium, are applied to suitable carriers. In the lean, i.e. oxygen-rich atmosphere, the nitrous oxides are oxidated under the effect of the noble metal catalyst, absorbed in the catalyst forming nitrates such as for example barium nitrate, and thus removed from the exhaust gas flow. Regular brief “richening” of the exhaust gas causes these reactions to proceed in the opposite direction, whereby the NOx molecules are returned to the exhaust gas flow and the reducing components present in the rich atmosphere, such as CmHn and/or CO, are further reduced.
When the absorption capacity of the NOx storage catalyst is exhausted, the engine electronics set a rich, substoichiometric, reducing exhaust gas mixture for a few seconds. In this brief regeneration mode, the NOx temporarily stored in the catalyst is reduced to oxygen and hence the NOx storage catalyst is prepared for the next storage cycle. This procedure makes it possible to minimize the pollutant emissions from internal combustion engines operated with an air surplus, and observe pollutant limits.
Enrichment for performing such a regeneration mode of the NOx storage catalyst can be achieved by late fuel injection, by changing the ratio of the fuel quantity on main injection to the fuel quantity on post injection, by means of intake air throttling, by increased exhaust gas recirculation rates, or by other measures.
The duration and frequency of the regeneration modes are determined by the engine control unit as a function of the stored nitrous oxide quantity, exhaust gas temperature, exhaust gas mass flow and other parameters.
DE 10 2015 208 093 A1 discloses an arrangement for exhaust gas aftertreatment in an exhaust system, wherein the arrangement comprises an NOx storage catalyst, a three-way catalyst and, arranged upstream thereof, an SCR catalyst for selective catalytic reduction of nitrous oxides contained in the exhaust gas supplied to the SCR catalyst, wherein an oxygen storage capacity component (OSC) is provided in the SCR catalyst which stores oxygen under operating conditions with a lean exhaust gas mixture, and in operating phases with a rich exhaust gas mixture provides oxygen to support the reduction of nitrous oxides at the SCR catalyst.
However, during the regeneration mode, there may not be sufficient oxygen present to convert all breakthrough hydrocarbons (HC) and/or carbon monoxide (CO) leaving the NOx storage catalyst.
The issue of regenerating an exhaust gas aftertreatment device in which breakthrough hydrocarbons and/or carbon monoxide are also converted is addressed by the present disclosure.
The present disclosure provides a method for operating an exhaust gas aftertreatment device for cleaning an exhaust gas flow of a motor vehicle with an internal combustion engine operated with oxygen surplus in normal mode, wherein an oxygen store arranged downstream of an NOx storage catalyst of the exhaust gas aftertreatment device receives oxygen in normal mode, and during a regeneration mode emits oxygen for converting breakthrough hydrocarbons and/or carbon monoxide, wherein the oxygen store is assigned to a particulate filter and/or an oxidation catalyst of the exhaust gas aftertreatment device, wherein the particulate filter and/or the oxidation catalyst is arranged downstream of the NOx storage catalyst. Thus, the present disclosure deviates from the proposal for converting all hydrocarbons and/or carbon monoxide completely during the regeneration mode in the NOx storage catalyst, and instead proposes only providing oxygen for this further downstream of the NOx storage catalyst. Thus, breakthrough hydrocarbons and/or carbon monoxide can be converted after leaving the NOx storage catalyst.
According to one form of the present disclosure, a coating containing cerium dioxide and/or zirconium dioxide is used as an oxygen store. Cerium dioxide is an oxide of the rare earth metal cerium and zirconium dioxide (formerly known as zirconic acid or zirconia) are compounds of the element zirconium. Cerium dioxide is used for example in catalysts of motor vehicles, and on an oxygen deficit oxidates carbon monoxide and surplus hydrocarbons. Also, the coating containing cerium dioxide and/or zirconium dioxide has a high oxygen storage capacity.
According to a further form, a regeneration mode is ended when a comparison of an oxygen value with a target oxygen value shows that the oxygen value is equal to or less than the target oxygen value. Comparison of the oxygen value with the target oxygen value establishes whether the oxygen store has become exhausted and therefore no longer provides sufficient oxygen for the conversion of breakthrough hydrocarbons and/or carbon monoxide. By ending regeneration mode, a switch occurs to lean mode in which the NOx storage catalyst again absorbs hydrocarbons and/or carbon monoxide, and thus no breakthrough of these substances is to be feared. Thus undesirable emissions are avoided.
According to a further form, the oxygen is determined using a model during regeneration mode. Therefore, the oxygen value is not determined by measurement, e.g. with an oxygen sensor, but indirectly using the model. The model links together measurement values for the temperature, e.g. the exhaust gas temperature which is indicative of the temperature of the oxygen store, the mass flow and the lambda value, in order to determine a value representative of the oxygen value as an output parameter. Thus the oxygen value can be determined without using an oxygen sensor.
According to a further form, the model is configured to take into account by adaptation aging effects of the exhaust gas aftertreatment device. For this, the model also supplies a lambda simulation value which is compared with a lambda value measured downstream of the particulate filter and/or the oxidation catalyst. Aging effects can lead to a slow reduction in the storage capacity of the oxygen store, and hence also of the oxygen content, which leads to a change in the measured lambda value. This leads to a shortening of the duration of the regeneration mode, since during a shortened regeneration mode, breakthrough hydrocarbons and/or carbon monoxide can be converted.
The present disclosure furthermore concerns an exhaust gas aftertreatment device and a motor vehicle with such an exhaust gas aftertreatment device.
Further areas of applicability will become apparent from the description provided herein. It should be understood that the description and specific examples are intended for purposes of illustration only and are not intended to limit the scope of the present disclosure.
In order that the disclosure may be well understood, there will now be described various forms thereof, given by way of example, reference being made to the accompanying drawings, in which:
The drawings described herein are for illustration purposes only and are not intended to limit the scope of the present disclosure in any way.
The following description is merely exemplary in nature and is not intended to limit the present disclosure, application, or uses. It should be understood that throughout the drawings, corresponding reference numerals indicate like or corresponding parts and features.
The internal combustion engine 4 in the present exemplary form is a diesel engine, i.e. the diesel engine is operated in normal mode with an oxygen surplus (λ>1). By deviation, the internal combustion engine 4 may also be configured as a petrol engine in lean mode to increase the engine efficiency.
In the present exemplary form, the exhaust gas aftertreatment device 6 connected downstream of the internal combustion engine 4 in the exhaust gas flow direction has an NOx storage catalyst 8.
By deviation from the exemplary form shown in
The NOx storage catalyst 8 is configured to store NOx (nitrous oxides). It has a structure with a suitable carrier with a noble metal catalyst such as platinum, and an NOx storage component e.g. an earth alkali metal such as barium.
The internal combustion engine 4 has an assigned control unit (not shown) which causes a switch from operation with oxygen surplus to a substoichiometric operation and vice versa, as will also be explained in more detail later. For this, the control unit has hardware and/or software components.
A particulate filter 10 is arranged downstream of the NOx storage catalyst 8. In the present exemplary form, the particulate filter 10 is formed as a diesel particulate soot filter for reducing the particles present in the exhaust gas. The particulate filter 10 is also known as a diesel particulate filter (DPF), corresponding to the particle origin, or a soot particulate filter (RPF), corresponding to the particle composition.
The particulate filter 10 downstream of the NOx storage catalyst 8, like the NOx storage catalyst 8, is arranged as close as possible to the internal combustion engine 4 in order to guarantee rapid heating of the NOx storage catalyst 8 and particulate filter 10, so that the two components are ready for operation quickly.
Furthermore, in the present exemplary form, an oxygen store 12 is provided which absorbs and temporarily stores oxygen during normal operation with a lean mixture, and emits oxygen during a regeneration mode with a rich mixture.
In the present exemplary form, the oxygen store 12 is assigned to the particulate filter 10 and formed by a coating which, in the present exemplary form, contains cerium dioxide (CeO2) and/or zirconium dioxide (ZrO2).
Reference is now made additionally to
It is evident that in this example, the oxygen storage capacity S increases almost linearly with the temperature T in a temperature range from 150° C. to 500° C., and then increases further linearly with a smaller gradient from higher temperatures T.
Reference is now also made to
The model 14 links together measurement values for the temperature T, such as e.g. the exhaust gas temperature which is indicative of the temperature of the oxygen store 10, the mass flow mflow and the lambda value λeng on the downstream side of the internal combustion engine 4, in order to determine a value representative of the oxygen value O2LNT as an output parameter, e.g. according to the following equation:
dO2LNT/dt=f1(1−λ,λ<1,T,mflow,O2LNT).
Furthermore, the model 14 is configured to also provide a lambda simulation value λmod which is compared with the lambda value λmeas measured downstream of the particulate filter 10, so that aging effects can be taken into account.
For this, the model 14 links together, as well as the measured values for the lambda value λeng downstream of the internal combustion engine 4, the temperature T, the mass flow mflow and the oxygen value O2LNT, e.g. according to the following equation:
λmod=f2(λeng,mflow,O2LNT).
The model 14 may be implemented on a control unit (not shown), which for this has hardware and/or software components.
With additional reference now to
In normal mode, the internal combustion engine 4 is operated in the part load range with a lambda value of the supplied mixture which is greater than one, i.e. with an oxygen surplus. During normal mode, the NOx storage catalyst 8 absorbs nitrous oxides from the exhaust gas flow, and the oxygen store 12 absorbs oxygen from the exhaust gas flow which has passed through the NOx storage catalyst 8, and temporarily stores this until the oxygen store 12 is full (OSC full in
In order to achieve a regeneration of the NOx storage catalyst 8, a regeneration mode R is performed. The duration and frequency of the regeneration mode R are determined by the control unit, e.g. as a function of the stored nitrous oxide quantity, the exhaust gas temperature, the exhaust gas mass flow and other parameters, and then initiated.
For this, the control unit actuates the internal combustion engine 2 such that the exhaust gas has a lambda value of less than one, in order to regenerate the NOx storage catalyst 8. For this, the control unit e.g. changes the time of fuel injection to achieve a late fuel injection, changes the ratio of the fuel quantity on main injection to the fuel quantity on post injection, changes the position of the throttle valve (air throttling), or increases the exhaust gas recirculation rate.
However, during regeneration mode R, the NOx storage catalyst 8 may not contain sufficient oxygen to convert completely all hydrocarbons and/or carbon monoxide leaving the NOx storage catalyst 8.
Such hydrocarbons and/or carbon monoxide leaving the NOx storage catalyst 8 are known as breakthrough hydrocarbons and/or carbon monoxide.
The breakthrough hydrocarbons and/or carbon monoxide reach the particulate filter 10 with the oxygen store 12. During the regeneration mode R, the oxygen store 12 emits the oxygen temporarily stored and thus allows conversion of the breakthrough hydrocarbons and/or carbon monoxide.
The control unit ends the regeneration mode R when a comparison of the oxygen value O2LNT with a predefined target oxygen value O2Targ shows that the oxygen value O2LNT is equal to or less than the target oxygen value O2Targ.
This provides that a sufficient minimum quantity of oxygen is available to convert the breakthrough hydrocarbons and/or carbon monoxide. If however the oxygen quantity is below this minimum level, the result is a rise in the hydrocarbon and carbon monoxide concentration, as indicated in
The oxygen value O2LNT is determined using the model 14. Furthermore, the model 14 provides the lambda simulation value λmod.
The lambda simulation value λmod is compared with the lambda value λmeas measured downstream of the particulate filter 10, so that aging effects can be detected and taken into account. For this, the difference is formed between the measured lambda value λmeas and the lambda simulation value λmod, and parameters of the model 14 adapted accordingly.
Aging effects, in particular of the oxygen store 12, may lead to slow reduction in the storage capacity of the oxygen store 12 and hence also in the oxygen content, which leads to a change in the measured lambda value λmeas.
Thus an age-induced tracking in the oxygen value O2LNT supplied by the model 14 is achieved, and operation with insufficient oxygen reserves is avoided. Aging leads to a reduction in the oxygen storage capacity of the oxygen store 12. Thus only a reduced oxygen quantity is available during regeneration mode. This leads to a shortening of the duration of the regeneration mode, because sufficient oxygen is available only for a shorter regeneration mode. Thus, a sufficient minimum quantity of oxygen is provided for converting breakthrough hydrocarbons and/or carbon monoxide.
| Number | Date | Country | Kind |
|---|---|---|---|
| 10 2016 221 272 | Oct 2016 | DE | national |
| Number | Name | Date | Kind |
|---|---|---|---|
| 20030005685 | Lewis | Jan 2003 | A1 |
| 20130028818 | Eckhoff | Jan 2013 | A1 |
| Number | Date | Country | |
|---|---|---|---|
| 20180119593 A1 | May 2018 | US |
