An exhaust gas system for a diesel engine is known from EP 488 386 B1.
Likewise, an internal combustion engine including an exhaust gas system became known from DE 10 2007 053 130, in which case an additional vaporizer is used.
Moreover, a method is known from WO 9922129 for operating a piston-type internal combustion engine including a direct fuel injection system and an exhaust aftertreatment device.
It is disadvantageous here, for example in the variant having the additional vaporizer, that additional elements, which can malfunction, are necessary, which generate additional costs.
It is an object of the present invention to provide a device and a method which eliminate the above-mentioned disadvantages and also to develop a strategy to obtain maximum particulate matter burn-off rates in the diesel particulate filter.
The object is achieved by the combination of the throttle valve optimization:
The new approach allows the maximization of the so-called burn-off rate of particulate matter in the diesel particulate filter instead of maximizing the temperature upstream from the diesel particulate filter as previously. Intake-side throttling effectuates on the one hand an exhaust gas temperature increase, and on the other hand a reduction of the residual oxygen proportion in the exhaust gas due to lack of air (in comparison to the unthrottled case) during combustion. Due to the new approach, it would be possible to optimize the burn-off rate in the diesel particulate filter (“DPF”) in a certain throttle valve adjustment range and to minimize the time for the service regeneration. It should be possible to optimize the throttle valve setting to a maximum particulate matter burn-off rate by using the approach described. This is a physical predictive model maximization of the soot burn-off rate with the aid of regulation via a throttle valve.
The second approach allows a targeted regulation of the engine by using a fuel unburned post injection (if an oxidation catalytic converter is present) in such a way that a service regeneration is successfully concluded after 30 minutes. The advantage would be the adjustment of the system to environmental conditions and poorly insulated exhaust gas systems, for example exhaust gas lines from the engine turbine to the exhaust aftertreatment system.
The fuel is injected torque neutrally during the expansion stroke. Under ideal conditions, the fuel is injected after the combustion stroke, vaporized, and provided after the exhaust stroke to the DOC as an oxidizer in order to increase the exhaust gas temperature due to the exothermic reaction process. Fuel is torque neutrally injected during the exhaust stroke (expansion stroke).
Using the plausibility examinations depicted in the following, it is possible to adjust the exhaust gas oxygen content and the DPF temperature into a range in such a way that a service regeneration is enabled in all environmental boundary conditions or in exhaust aftertreatment systems which are not optimally insulated.
As preparation for carrying out a service regeneration, the vehicle is operated at a stationary rotational speed and a corresponding base load suitable to the hydraulic power unit. In the first step, injection parameters (pilot injection, main injection, and post injection timing and pilot and post injection amounts and rail pressure) are adjusted in such a way that the efficiency of the engine declines and thus the exhaust gas temperature is increased. In the second step, the intake—side throttle valve is regulated to a minimum pressure in the charge air pipe to further degrade the efficiency and thus to further increase the exhaust gas temperature of the engine. The throttle valve emerges as the dominant temperature increase effect for increasing the exhaust gas temperature in comparison to adjusting the injection parameters. It is thus possible to maximize the exhaust gas temperature by throttling the throttle valve within a possible and safe operation of the engine. The intended maximized temperature range upstream from the diesel particulate filter lies between 550° C. and 620° C. in order to reduce the global DPF load from 4 g/l to below 1 g/l in the diesel particulate filter within 30 minutes.
For certain applications using diesel particulate filters, it may result, under certain circumstances, that the soot or particulate filter load exceeds a critical load limit. A possible counter measure to reduce a filter load which is too high to an acceptable level, in order to allow a normal driving operation, is on the one hand an engine operation at high stationary engine output or, if this is not possible, a so-called service regeneration. During this service regeneration, the vehicle is not operational. With regard to the proposed approach the device is operated at a stationary working rotational speed and at a base load. The base load is dependent on the specific hydraulic power unit of the vehicle flange-mounted to the diesel engine. Injection parameters and a throttle valve (downstream from the charge air cooler, ITV=intake throttle valve) are parameterized during a service regeneration in such a way that the exhaust gas temperature is maximized downstream from the turbine or upstream from the diesel particulate filter. Due to the “high” exhaust gas temperatures and the residual oxygen in the exhaust gas, soot or solid particulates are oxidized in the diesel particulate filter and the filter load is thus reduced. The underlying mechanism for reducing the soot in the diesel particulate filter is designated as “active regeneration” in this case, i.e. soot is oxidized exclusively using residual oxygen in the exhaust gas at temperatures above 500° C. The duration of a service regeneration is measured in a time-controlled manner in order to reduce the DPF load to a lower load threshold.
The DPF temperature, the residual oxygen concentration in the exhaust gas, and also the particulate load are exclusively significant for the quantification of the particulate burn-off rate during an active regeneration. Using a phenomenological model approach developed by us, see Equations 1 and 2, the above statement could be numerically and experimentally confirmed. In addition, it could be shown that the phenomenological approach, independent of DPF geometry and cell density substrate, achieves very good results in comparison with experimental results. The burn-off rate is given according to Equations 1 and 2 as:
where [O2] is the oxygen concentration and f(T) is a temperature term, msoot is the DPF load at a specific point in time t, and a, b, c, and d correspond to calibration parameters. Under the premise that the oxygen concentration [O2] and also the temperature T in the diesel particulate filter (DPF) may be regarded as constants, the standardized burn-off rate dmsoot/dt/msoot likewise describes a constant, see equation 3.
Under these assumptions, Equation 4 describes the resolution of the differential equation of Equation 1, where m0 corresponds to the DPF load at point in time t=0 (start of the service generation). Under the assumption that the particulate mass flow emitted by the engine into the DPF may be assumed to be negligibly small in comparison to the burn-off rate, Equation 4 describes the DPF particulate load for an arbitrary point in time t.
By solving Equation 4 for time t, a time criterion may be defined for the DPF burn-off, which depends exclusively on the start DPF load m0=msoot (t=0), the end load msoot(t), the DPF temperature T, and the exhaust gas oxygen concentration [O2].
Throttle Valve Optimization
In addition, the DPF temperature and the exhaust gas oxygen concentration dependency corresponding to the results from
Plausibility Check
In order to define a time-related criterion as a function of the DPF temperature and the exhaust gas oxygen concentration, in which a DPF service regeneration may be defined as successful or as unsuccessful, the following method is used. For example, 4 g/l as a maximum acceptable DPF load (soot per volume unit) and <1 g/l as the DPF regeneration target value are required. With the aid of equation 5, the corresponding burn-off times are calculated for DPF temperatures from 300° C. to 620° C. and exhaust gas oxygen concentrations of 0.5% to 20%. The calculated results are shown in
Number | Date | Country | Kind |
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10 2012 022 712 | Nov 2012 | DE | national |
Filing Document | Filing Date | Country | Kind |
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PCT/EP2013/003295 | 11/2/2013 | WO | 00 |
Publishing Document | Publishing Date | Country | Kind |
---|---|---|---|
WO2014/079535 | 5/30/2014 | WO | A |
Number | Name | Date | Kind |
---|---|---|---|
5343702 | Miyajima et al. | Sep 1994 | A |
6865885 | Kitahara | Mar 2005 | B2 |
6968732 | Nakoji | Nov 2005 | B2 |
7155899 | Beer et al. | Jan 2007 | B2 |
7178327 | Miyashita | Feb 2007 | B2 |
7246595 | Hoare | Jul 2007 | B1 |
20030033800 | Tonetti | Feb 2003 | A1 |
20050086933 | Nieuwstadt | Apr 2005 | A1 |
20050257771 | Nakayama et al. | Nov 2005 | A1 |
20060005534 | Wirth et al. | Jan 2006 | A1 |
20060096572 | Satou et al. | May 2006 | A1 |
20060130465 | Sun | Jun 2006 | A1 |
20080276604 | Hosaka | Nov 2008 | A1 |
20110047982 | Chen et al. | Mar 2011 | A1 |
Number | Date | Country |
---|---|---|
19717805 | Oct 1998 | DE |
10259052 | Apr 2004 | DE |
102007053130 | May 2009 | DE |
0272619 | Jun 1988 | EP |
488386 | Jun 1992 | EP |
1 384 868 | Jan 2004 | EP |
1531249 | May 2005 | EP |
1 669 574 | Jun 2006 | EP |
WO 9922129 | May 1999 | WO |
WO 2010007282 | Jan 2010 | WO |
Number | Date | Country | |
---|---|---|---|
20150292426 A1 | Oct 2015 | US |