IPC분류정보
국가/구분 |
United States(US) Patent
등록
|
국제특허분류(IPC7판) |
|
출원번호 |
US-0667761
(2005-10-20)
|
등록번호 |
US-7474953
(2009-01-06)
|
우선권정보 |
AT-A 1986/2004(2004-11-25); AT-A 2072/2004(2004-12-09); AT-A 795/2005(2005-05-10) |
국제출원번호 |
PCT/AT05/000416
(2005-10-20)
|
§371/§102 date |
20070515
(20070515)
|
국제공개번호 |
WO06/055992
(2006-06-01)
|
발명자
/ 주소 |
- Hülser,Holger
- Krickler,Manfred
|
출원인 / 주소 |
|
대리인 / 주소 |
|
인용정보 |
피인용 횟수 :
12 인용 특허 :
3 |
초록
A process for determining particle input into a particle filter arranged in the exhaust fume stream of an internal combustion engine makes it possible to determine the mass of deposited particles by taking into account particle and nitrogen oxide emission.
대표청구항
▼
The invention claimed is: 1. Method for determining particulate emissions in the exhaust gas stream of an internal combustion engine, comprising the following steps: preparing an emissions model based on an operational characteristic map of the engine; measuring actual particulate emissions in the
The invention claimed is: 1. Method for determining particulate emissions in the exhaust gas stream of an internal combustion engine, comprising the following steps: preparing an emissions model based on an operational characteristic map of the engine; measuring actual particulate emissions in the exhaust gas stream during a fixed or variable measuring interval and integrating particulate emissions over the measuring interval; computing ideal particulate emissions during the measuring interval by means of the emissions model and integrating ideal particulate emissions over the measuring interval; comparing measured actual particulate emissions and computed ideal particulate emissions; determining a correction factor based on the difference of measured actual particulate emissions and computed ideal particulate emissions; and taking into account the correction factor when determining ideal particulate emissions from the emissions model. 2. Method according to claim 1, wherein a uniform correction factor is chosen for all operating points of the internal combustion engine. 3. Method according to claim 1, wherein different correction factors are chosen for different operating regions. 4. Method according to claim 3, wherein the different correction factors are determined on the basis of a correction characteristic map. 5. Method according to claim 3, wherein the different correction factors are determined taking into account the frequency distribution of operating points of the internal combustion engine. 6. Method according to claim 1, wherein a new correction factor f_K is computed from an old value of the correction factor f_K_alt and a ratio soot_ratio between actually measured and computed ideal particulate emissions, using the formula f_K=f1*f_K_alt ×(1-f1)/soot_ratio, where the coefficient f1 has a value between 0 and 1. 7. Method according to claim 6, wherein the coefficient f1 has a value between 0.85 and 0.95. 8. Method according to claim 1, wherein the correction is carried out only if its value lies within a plausibility interval. 9. Method for determining a particle load deposited in a particulate filter located in an exhaust duct of an internal combustion engine, including the following steps: preparing an emissions model for particles which is based on a characteristic map; preparing at least one, characteristic-map-based emissions model for nitrogen oxides; preparing a temperature-dependent model for the oxidation of soot particles by nitrogen oxides; determining at least one value selected from the group theoretical particle mass or particle concentration for at least one operating point using the emissions model for particles; determining at least one value selected from the group mass or concentration of nitrogen oxides for at least one operating point using the emissions model for nitrogen oxides; determining at least one value selected from the group negative equivalent particle mass or negative equivalent concentration for the nitrogen oxide mass or concentration determined in the preceding step, using the oxidation model of soot particles by nitrogen oxides; determining at least one value selected from the group effective particulate mass or concentration using the emissions model for particles and the negative equivalent particle mass and/or concentration; and accumulating the effective particulate mass or concentration in a model of the particulate filter. 10. Method according to claim 9, wherein separate characteristic-map-based emissions models for NO and NO2 emissions are prepared, and wherein NO and NO2 emissions are determined for the at least one operating point, and wherein effective particulate masses or concentrations are determined on the basis of the NO and NO2 emissions. 11. Method according to claim 9, wherein a temperature of the particulate filter is measured at least at one point and that the negative equivalent particle mass or the negative equivalent particle concentration is determined depending on the temperature of the particulate filter. 12. Method according to claim 11, wherein the temperature of the particulate filter is determined by measuring the exhaust gas temperature upstream of the particulate filter. 13. Method according to claim 9, wherein for determination of the effective particulate mass it is taken into account that the nitrogen oxides in the exhaust duct will oxidize the soot particles present in the exhaust gas better than the soot particles already deposited in the particulate filter. 14. Method according to claim 13, wherein the value for the effective particulate mass is limited by a lower bound. 15. Method for controlling the regeneration of an exhaust treatment device, especially a particulate filter, by means of a characteristic-map-based computational model, where the exhaust treatment device is divided into at least two cells, and where a deposit load state of each cell is determined by means of a deposition model and a regeneration process for the exhaust treatment device is initiated depending on the deposit load state, wherein a deposit state index is determined which is based on the deposit load state of at least one cell, and that the regeneration process is initiated depending on the value of the deposit state index. 16. Method according to claim 15, wherein at least two cells are defined one behind the other in flow direction. 17. Method according to claim 15, wherein the cells are defined to be at least approximately of equal size. 18. Method according to claim 15, wherein at least for a group of cells two threshold values each are defined, and that the deposit state index is determined depending on the frequency with which the threshold values are exceeded. 19. Method according to claim 18, wherein the exceeding of a higher threshold value has greater influence on the deposit state index than the exceeding of lower threshold values. 20. Method according to claim 15, wherein the particulate load of the exhaust treatment device is divided into combustible and non-combustible particles, and that the deposit load of each cell is separately determined for combustible and non-combustible particles. 21. Method according to claim 20, wherein the regeneration of the exhaust treatment device is initiated only if the deposit load of one or more cells due to combustible particles exceeds a threshold value for combustible particles. 22. Method according to claim 15, wherein the deposit load state of each cell is determined depending on the nitrogen oxides present in the exhaust gas stream or depending on the temperature of the exhaust gas treatment device. 23. Method according to claim 15, wherein the deposition model divides the mass of particles entering each cell into a part which is deposited in the cell and a part which exits the cell. 24. Method for controlling the regeneration of an exhaust treatment device, especially a particulate filter, by means of a characteristic-map-based computational model, where the exhaust treatment device is divided into at least two cells and preferably at least five cells, and where the deposit load state of each cell is determined by means of a deposition model and a regeneration process for the exhaust treatment device is initiated depending on the deposit load state, wherein at least one threshold value for the maximum permissible deposit load state is defined for each cell, and wherein the regeneration process for the exhaust treatment device is initiated if the deposit load state of at least one cell exceeds the corresponding threshold value. 25. Method according to claim 24, wherein at least two cells are defined one behind the other in flow direction. 26. Method according to claim 24, wherein the cells are defined to be at least approximately of equal size. 27. Method according to claim 24, wherein for each cell at least one threshold value for the maximum permissible deposit load state is defined. 28. Method according to claim 27, wherein the threshold values of at least two cells are defined to have different values, with the threshold value of an upstream cell being defined smaller than the threshold value of a downstream cell. 29. Method according to claim 24, wherein a regeneration process is initiated if the deposit load state of at least one cell exceeds the corresponding threshold value. 30. Method according to claim 24, wherein a regeneration process is initiated if a mean value of the deposit load states of a plurality of cells exceeds the corresponding threshold value. 31. Method according to claim 24, wherein a deposit state index is determined based on the deposit load state of at least one cell, and that the regeneration process is initiated depending on the deposit state index. 32. Method according to claim 24, wherein at least for a group of cells two threshold values each are defined, and that the deposit state index is determined depending on the frequency with which the threshold values are exceeded. 33. Method according to claim 32, wherein the exceeding of a higher threshold value has greater influence on the deposit state index than the exceeding of lower threshold values. 34. Method according to claim 24, wherein the particulate load of the exhaust treatment device is divided into combustible and non-combustible particles, and that the deposit load of each cell is separately determined for combustible and non-combustible particles. 35. Method according to claim 34, wherein the regeneration of the exhaust treatment device is initiated only if the deposit load of one or more cells due to combustible particles exceeds a threshold value for combustible particles. 36. Method according to claim 24, wherein the deposit load state of each cell is determined depending on the nitrogen oxides present in the exhaust gas stream or depending on the temperature of the exhaust gas treatment device. 37. Method according to claim 24, wherein the deposition model divides the mass of particles entering each cell into a part which is deposited in the cell and a part which exits the cell.
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