DE102014019427A1 - Process for cleaning diesel engine exhaust gases - Google Patents

Abstract

A process is described for passing the exhaust gas to be purified through a diesel oxidation catalyst (DOC) for the oxidation of gaseous residual hydrocarbons (HC) and of carbon monoxide (CO) to carbon dioxide (CO2) and for the at least partial oxidation of nitrogen monoxide (NO) contained in the exhaust gas to nitrogen dioxide (NO2) containing exhaust line.

Description

The invention relates to a process for the purification of diesel engine exhaust gases.

New generation engines show ever greater power output per stroke volume. This means that, especially when smaller power levels are applied, colder exhaust gas temperatures always occur, in which the safe operation of a "classic" exhaust aftertreatment system with a SCR catalytic converter remote from the engine can no longer be guaranteed.

Particularly in the low-load range, deposits from the crystallization of urea and urea by-products can hardly be avoided when metering in untempered urea water solution (HWL) into the exhaust gas. The resulting deposits can lead to blockage of the exhaust system and thus to the failure of the equipment during continuous operation in the lower part load range. Also, a sufficient Entstickungsleistung the SCR system in the low load range can no longer be guaranteed if the HWL in the exhaust gas can not be worked up completely to the actual reducing agent ammonia for lack of sufficient exhaust gas temperatures.

This leads to state-of-the-art EAT systems today, such as systems according to the EP-B-1 054 722 to increase the SCR catalyst volumes to achieve adequate denitrification rates. However, this is usually incompatible with the available space.

Furthermore, for engines of new design, a particle number limit applies. These limits can no longer be met without the introduction of a closed wall flow filter.

The DE 103 48 800 discloses a method for controlling a reductant delivery system having at least one heating element. The delivery system is connected upstream with an SCR catalyst. In the air assisted injection of the reductant into the delivery system, a vaporized mixture of air and the reductant is formed over the heated element which is introduced into an exhaust gas mixture entering the SCR catalyst. The reductant used is aqueous urea solution. The entire feed system including mixing unit for HWL and air and heating element / evaporator unit is downstream of the SCR catalyst in the exhaust gas pipe leading downstream of the engine outlet integrated. The amount of heat necessary for the evaporation of the HWL-air mixture is generated electrically with the aid of the 12 V battery current.

The DE 10 2007 029 674 discloses an assembly for nitrogen oxide reduction in an oxygen-containing gas flow, in particular an exhaust system of an internal combustion engine, with an arranged in a nitrogen oxides and oxygen gas line SCR catalyst, a reaction reactor, which converts an ammonia precursor containing solution into an ammonia solution, and a downstream of the reaction reactor, formed as a separate component evaporation unit in which the ammonia solution is evaporated before introduction into the gas line upstream of the SCR catalyst. The reaction of the solution containing an ammonia precursor (preferably urea-water solution) into an ammonia solution takes place according to the invention using microwaves. In front of the evaporation unit for ammonia solution, which is designed as a separate component, a heat exchanger for heating the ammonia solution can be connected upstream in order to reduce the energy required for evaporation, for example by using the heat of the exhaust gas recirculation line. The evaporator itself is an electrically operated heating element.

The DE 10 2007 042 836 discloses a device for exhaust aftertreatment of a motor vehicle by means of an ammonia-releasing liquid, such as urea water solution, comprising a reservoir for storing the liquid, wherein a temperature control is provided for controlling the temperature of the liquid. The temperature control is associated with a cooling circuit of the motor vehicle for cooling the liquid. This may be the cooling circuit of the internal combustion engine or an air conditioning circuit. The tempering device is designed as a separate component. By means of tempering the liquid can be heated and their freezing can be prevented or the liquid can be heated to a favorable temperature level, which results in a particularly good emission control.

The DE 10 2009 009 538 discloses a system for controlling a fluid additive for an exhaust system of an internal combustion engine, preferably urea water solution, characterized by Means for heat exchange between the additive and a refrigerant circuit of a refrigerant system, in particular an air conditioner.

The Indian DE 10 2007 011 184 described development is based on the object to further reduce the emission content of internal combustion engines, especially diesel engines, and to minimize the space required to treat the exhaust gas. To solve this problem, a heat exchanger for cooling exhaust gas of an internal combustion engine of a motor vehicle for the return of exhaust gas to the internal combustion engine is disclosed. This heat exchanger has at least one first flow channel for flowing through with at least one first fluid for cooling and at least one second flow channel for flowing through with a second fluid to be cooled, and a housing for receiving the at least one first flow channel and the at least one second flow channel. The housing has at least one inflow section for the inflow of the second fluid into the heat exchanger and at least one outflow section for the outflow of the second fluid from the heat exchanger. The heat exchanger is characterized by at least one device for transferring a liquid urea solution into at least ammonia gas.

The WO 2012/022687 discloses a method for operating an exhaust aftertreatment device having at least one reservoir for a reductant and at least one reductant supply device, the method comprising at least the following steps: a) checking a fill level of the at least one memory; b) checking the current exhaust gas mass flow; c) supplying reducing agent when the level of the at least one store is below a minimum level and the exhaust gas mass flow is in a low load range. In a particular embodiment, at least one of the following actions is performed in step c): heating at least the exhaust gas mass flow or the reducing agent and supplying reducing agent. In this case, the heat supply to the reducing agent can be ensured or improved by external electric heaters.

The DE 10 2009 025 135 discloses a device for vaporizing a urea water solution comprising a urea water solution delivery channel extending through at least a first zone and a second zone for introducing thermal energy, the two zones being separately heatable, and the delivery channel in the second zone first in a second entrance area a meandering course and then identifies a straight course. In the first zone, the urea water solution is preheated to a temperature in the range of 100 ° C to 180 ° C, in the second zone at a temperature of 420 ° C to 490 ° C evaporated.

The DE 10 2008 012 087 discloses an evaporation unit for generating an ammonia-comprising gas stream from urea water solution, which is also carried out as a separate component.

Prior art industrial engines are typically provided with catalytically active exhaust aftertreatment (ANB) systems according to the above EP-B-1 054 722 - or also called "SCRT ^® systems", consisting of DOC / (c) DPF + SCR / ASC with metered addition of urea water solution (HWL) before the SCR / ASC catalyst - operated to meet the applicable emission regulations (Tier4 final / EU stage IV and subsequent).

For the ANB system to operate with the required purification efficiency, minimum exhaust gas temperatures and catalyst operating temperatures of 230 ° C and more are required.

In low-load operating conditions, the required minimum exhaust gas temperatures can only be provided by means of engine thermal measures (eg throttling of the engine). The energy that is introduced into the exhaust to provide the necessary exhaust gas temperatures is lost to the powertrain. Reduced drive efficiency of the engine and increased fuel consumption and thus also increased CO ₂ emissions are the result.

A particularly large negative influence on the fuel consumption has the regeneration of the closed diesel particulate filter. For the controlled burnup of the soot stored in the filter, exhaust gas temperatures of approx. 600 ° C required. In order to achieve this, in addition to passive regeneration, active measures such as, for example, additional post fuel injection and exothermic conversion of the resulting unburned hydrocarbons to the DOC or active regeneration measures, for example by means of fuel-operated burners, are generally provided EP-A-2 177 728 . EP-A-2 192 279 respectively. WO 2010/139429 necessary.

To operate the SCR system, a urea water solution containing 32.5% urea is typically employed as the reductant.

In order to liberate ammonia, 67.5% of water must first be evaporated and the urea hydrolyzed to ammonia and CO ₂ .

In current systems, the SCR required for generating the reducing agent ammonia urea aqueous solution (urea water solution HWL, trade name AdBlue ^®) injected in liquid, untemperiertem state anstromseitig to the SCR catalyst in the exhaust gas. The amount of heat needed to completely convert the HWL into the gas phase with (quantitative) release of ammonia (= urea treatment) must be provided completely by the hot exhaust gas.

However, especially in low-load operating points, the amount of heat present in the exhaust gas is often not sufficient to completely treat the injected urea-water solution (HWL), which is required for complete reduction of the nitrogen oxides also present in the exhaust gas. The result is deposits of urea and urea secondary products such as isocyanic acid, cyanuric acid and melamine in the exhaust system (crystallization), which can lead to the possibly complete blockage of the exhaust system, as well as loss of revenue in the SCR reaction due to the incomplete provision of the nitrogen oxide reduction required stoichiometric amount of ammonia.

It is an object of the present invention to provide a method for purifying diesel engine exhaust gases which does not have the above-described disadvantages of present-day methods, in particular when the internal combustion engine is operating in the low-load range, and which has improved energy efficiency and at the same time the highest possible cost-efficiency of the overall system.

This object is achieved by a method for purifying diesel engine exhaust gases with the following method steps:
Passing the exhaust gas to be purified through a diesel oxidation catalyst (DOC) for the oxidation of gaseous residual hydrocarbons (HC) and of carbon monoxide (CO) to carbon dioxide (CO ₂ ) and for the at least partial oxidation of nitrogen monoxide (NO) contained in the exhaust gas to nitrogen dioxide (NO ₂ ) ;
Adding to the engine preconditioned, ie heated to 80-90 ° C urea water solution (HWL) to the resulting from step a.) Exhaust gas and release of ammonia from the added urea by thermolysis and hydrolysis;
Passing the exhaust gas resulting from step b.) Through an SCR-catalytically activated particulate filter (SDPF) for reducing the particles contained in the exhaust gas and the nitrogen oxides contained in the exhaust gas; Passing the exhaust gas resulting from step c.) Through a selective ammonia oxidation catalyst (ASC) to reduce residual ammonia levels.

Preferably, the preconditioning of urea water solution on the engine by means of in DE 10 2014 001 879.2 disclosed device.

The dosage of conditioned, d. H. Pre-warmed urea water solution (HWL) into the exhaust system at a temperature of 80-90 ° C enables metering at lower exhaust gas temperatures (180-200 ° C) than with conventional metering procedures (200-230 ° C). Since for processing the HWL to ammonia less thermal energy must be entered, as in conventional systems, this advantage can be used instead of lowering the Dosierschwelltemperatur on the other to shorten the mixing distance before SDPF or before SCR catalyst.

The exhaust aftertreatment system arranged downstream of the engine downstream of the turbine comprises a DOC, a device for HWL metering, an SCR catalytically activated particulate filter (SDPF) and an ammonia oxidation catalyst, and optionally a second SCR catalytic converter arranged SDPF and ammonia oxidation catalyst (also: ammonia slip catalyst ASC).

By (partially) integrating SCR catalyst volume into the particulate filter, it is possible to downsize the ANB system compared to conventional systems. An improved heating characteristic of the ANB system after the cold start and significantly lower heat losses via the exhaust system are the result. In addition, space advantages result. The SCR catalyst, which is arranged downstream of the particulate filter in the flow direction of the exhaust gas, is used optionally when the SCR volume which can be integrated into the particulate filter is not sufficient to allow NO _x conversion of the entire system over the transit time (8000 Operating hours) of greater than 97%.

The method according to the invention particularly preferably comprises a passive regeneration concept for the SCR catalytically activated particulate filter (SDPF), which is described below. An additional standstill regeneration of the particulate filter is carried out as part of the service, as well as the monitoring of the exhaust backpressure via SDPF, in order to be able to perform so-called emergency shutdown regenerations in the case of insufficient Rußregenerationsraten outside the service intervals.

The SCR-catalytically activated particulate filter (SDPF) is operated in particularly preferred embodiments of the method according to the invention with a passive filter regeneration concept. This includes the burning-off of soot after the so-called ^CRT® reaction, in which the oxidation of the stored soot particles takes place with NO ₂ , which is generated in the first step of the process according to the invention over the DOC arranged upstream of the SDPF. ^CRT® reaction: C _n + 2n NO ₂ nCO ₂ + 2n NO

This CRT reaction is in competition with the SCR reaction. For the SCR reaction, there are three reaction mechanisms that proceed at different reaction rates (RG): Standard SCR: 4NO + 4NH ₃ + O ₂ 4N ₂ + 6H ₂ O medium RG almost SCR: NO + NO ₂ + 2NH ₃ 2N ₂ + 3H ₂ O high RG slow SCR: 6NO ₂ + 8NH ₃ 2N ₂ + 12H ₂ O low RG

In order to provide a sufficient amount of NO ₂ for the soot combustion for passive regeneration of the particulate filter, the upstream DOC must provide more than 50% NO ₂ in NO _x at operating points up to an exhaust gas temperature of 350-375 ° C. The NO ₂ excess stands for the soot combustion available when the "CRT ^® reaction" is faster than the "slow-SCR" reaction, so that a passive filter regeneration is ensured.

At a DOC operating temperature above about 300 ° C leaves the kinetically controlled range. The catalyst-producible NO ₂ concentration in the exhaust gas then no longer depends solely on the catalyst performance, but on the position of the thermodynamic equilibrium. At temperatures of more than 400 ° C, NO ₂ concentrations of more than 50% in NO _{x are} no longer producible: starting at 250 ° C, the soot oxidation begins with NO ₂ . From 300 ° C a passive regeneration of the particulate filter with high reliability is possible (source: C. Hagelüken et al, "Auto-Abatement Catalysts, 2nd ed., Expert Verlag 2005, p. 102 ). Under these conditions, the competition between SCR reaction and "CRT ^® reaction" can be handled, provided sufficiently high NO ₂ concentrations are provided.

If the amount of NO _{2 that} can be provided by the DOC is not sufficient to productively dissolve the competitive situation between SCR reaction on the one hand and soot regeneration on the other hand, it is possible to limit the denitration efficiency of the SCR catalytically activated filter by limiting the amount of reducing agent to be metered in to ensure sufficient passive regeneration of the particulate filter. In this case, in an alternative embodiment, a second metering point for urea water solution (HWL) is provided in front of a downstream (additional) SCR catalytic converter. By means of this second metering point preconditioned, ie, heated to 80-90 ° C urea water solution (HWL) is the resulting from step c.) Exhaust gas supplied to ensure the required Entstickungseffizienz the entire system of> 97%.

A further advantageous embodiment provides an industrial engine with an ANB system of DOC + SDPF + SCR / ASC, wherein instead of a device for metering urea water solution into the exhaust gas to be cleaned, a device for metering in gaseous ammonia is used. The preparation of the urea to ammonia takes place in such an embodiment in a motor attached to the reactor urea water solution is fed as educt and in which in a catalytic process by thermolysis of urea to isocyanic acid and ammonia and subsequent hydrolysis of the resulting isocyanic acid to ammonia and CO ₂ the processing of urea to ammonia is carried out independently of the prevailing operating conditions in the exhaust system.

Due to the outsourcing of the urea treatment to ammonia from the exhaust system and the direct dosing of ammonia in the ANB system, the temperature threshold for the metering of the reducing agent to well below 200-230 ° C, preferably lowered to temperatures in the range of 120-180 ° C. become.

The limitation of the aforementioned lower Temperaturdosierschwelle is in the range of the operating temperature window of the SCR catalyst. By metering gaseous ammonia, there is no risk of crystallization of urea and urea derivatives such as isocyanic acid, cyanuric acid or melamine, which result from the incomplete degradation of urea and can lead to complete blockage of the exhaust system at too low operating temperatures. Furthermore, there is no limitation of the Entstikkungseffizienz by incomplete urea treatment to ammonia in this process. Overdosage of reducing agent to compensate for incomplete urea processing at low load points becomes superfluous. A reduction of the ASC and / or the complete avoidance of the ammonia secondary emission of (allowable) 10 Vppm on average without ASC are possible.

The invention and the technical environment are explained below with reference to the figures. It should be noted that the invention is not limited to the subject matter of the figures. It shows schematically:

1 a preferred embodiment of the device for carrying out the method according to the invention,

2 the crankcase of an internal combustion engine with integrated HWL heat exchanger.

1 shows an internal combustion engine 1 with an exhaust system 2 and a urea-water solution tank 3 , In the exhaust system 2 in the flow direction of the exhaust gas is between DOC 5 and the SDPF 6 a NO _x sensor 9 and a HWL entry device arranged by the HWL heat exchanger 14 is fed. The HWL heat exchanger 14 can also use the HVL entry device between SDPF 6 and the SCR 7 supply with HWL. In the flow direction of the exhaust gas is an ammonia slip catalyst (ASC) 8th behind the SCR 7 , At the end of the exhaust line 2 is a NO _x sensor 9 arranged. In an alternative embodiment, it is provided that the HWL heat exchanger 14 essentially in a double-walled exhaust pipe 11 is arranged, the two NO _x sensors 9 wherein the one NO _x sensor 9 between DOC 5 and SDPF 6 and the other behind the ASC 8th is arranged.

In 2 becomes a crankcase of an internal combustion engine 1 with in the cooling circuit or water jacket 13 integrated HWL heat exchanger 14 shown. The HWL is located in the urea-water solution tank arranged in the region of the internal combustion engine 3 , The HWL is using liquid yarn delivery pump 12 in the region of the cooling water leading portion of the crankcase of the internal combustion engine 1 promoted, in which the HWL heat exchanger 14 is located and through which the HWL is heated. In an alternative embodiment, not shown, it is provided that the HWL heat exchanger 14 in the cylinder head of the internal combustion engine 1 is arranged. The heated HWL passes through the liquid yarn delivery pump 12 after leaving the HWL heat exchanger 14 in the metering device 15 , After the HWL the metering device 15 has left, she gets into the mixing section in the exhaust piping 16 in which it is heated further.

If desired, additional SCR catalyst volume can advantageously be integrated between the SCR-coated particulate filter and the ammonia oxidation catalyst. In this case, the ASC is applied as a downstream zone on the SCR catalyst. By (partial) integration of the SCR catalyst volume in the particulate filter, the overall space required by the exhaust aftertreatment system is still significantly lower than that of a conventional system according to EP-B-1 054 766 ,

The metering of preconditioned HWL into the exhaust line not only allows metering at lower exhaust gas temperatures than with conventional metering methods. Since the processing of the HWL to ammonia less thermal energy must be entered as in conventional systems, this advantage can be exploited for non-lowering the Temperaturdosierschwelle for shortening the mixing section.

Systems with SCR-coated filters, which are described in the prior art, especially in passenger car applications, are typically regenerated actively, for example by means of post-injection fuel injection and exothermic oxidation of the resulting hydrocarbons over a filter upstream of the diesel oxidation catalyst. In the method according to the invention, a passive regeneration of the particulate filter should take place. This requires sufficient amounts of NO ₂ in the exhaust gas before particulate filters. The upstream oxidation catalyst must therefore have high NO oxidation rates, so that there is a NO ₂ / NO _x ratio> 0.5 in the exhaust gas before SCR-coated particulate filter. In this case, it can be assumed that only NO ₂ , which is present in the ratio of 1: 1 in the exhaust gas before the SCR-coated filter, in the SCR reaction ("almost SCR "note different reaction rates !!). Any additional shares in NO ₂ are the soot burn after CRT ^® effect available.

At less optimal operating temperatures, in an alternative embodiment advantageously a second HWL metering point can be arranged between the SCR-coated particle filter and a downstream SCR / ASC. To ensure full passive regeneration, a substoichiometric amount of reductant is then provided before the SCR-coated filter. The residual denitrification takes place after a second HWL injection in the downstream SCR / ASC catalyst.

The term selective catalytic reduction (SCR) refers to a technique for the reduction of nitrogen oxides in exhaust gases of combustion plants, waste incinerators, gas turbines, industrial plants and engines. The chemical reaction on the SCR catalyst is selective, that is, it is preferable that the nitrogen oxides (NO, NO ₂ ) are reduced, while undesirable side reactions (such as the oxidation of sulfur dioxide to sulfur trioxide) are largely suppressed.

The reaction requires ammonia (NH ₃ ), which is released from the urea water solution mixed with the exhaust gas. The products of the reaction are water (H ₂ O) and nitrogen (N ₂ ). Chemically, the reaction is a comproportionation of the nitrogen oxides with ammonia to nitrogen. There are different types of catalysts. One type consists essentially of titanium dioxide, vanadium pentoxide and tungsten dioxide. The other type uses zeolites.

The method according to the invention provides for the integration of at least part of the SCR catalyst volume into the particulate filter volume by using an SCR catalytically activated particulate filter.

The inventive method also provides the preconditioning of the urea water solution (HWL) on hot engine components such as the cooling fins of an air-cooled internal combustion engine in a device for preconditioning of urea water solution. A further advantageous embodiment provides that the pre-conditioning or conditioning of the HWL in the field of high-energy cooling and / or lubricant flows takes place.

In vehicle technology, the SCR process is used to reduce nitrogen oxide emissions in diesel vehicles. With the help of this technology, commercial vehicles can meet the Euro V standard, agricultural vehicles meet the Tier 3b standard, and passenger cars meet the very stringent American BIN5 emission standard and the Euro 6 standard. This technology is also used to meet the emission standards US Tier4 final and EU Stage IV.

The ammonia required for the SCR reaction is not used directly, ie in pure form, but generated in the exhaust system from a 32.5 percent aqueous urea solution. The composition of the HWL is in the DIN 70070 regulated. This aqueous solution is placed in front of the SCR catalyst in the exhaust line, z. B. by means of metering pump or injector injected. Thermolysis and a hydrolysis reaction produce ammonia and CO ₂ from the urea-water solution. The ammonia thus produced can react in a special SCR catalyst at the appropriate temperature with the nitrogen oxides in the exhaust gas. The amount of injected urea depends on the engine's nitrogen oxide emissions and thus on the current speed and torque of the engine. The consumption of urea-water solution is dependent on the raw emission of the engine about 2 to 8% of the amount of diesel fuel used. It must therefore be carried along a corresponding tank volume. To achieve high NO _x reduction rates, it is important that the urea water solution (AdBlue ^® ) is proportioned in proportion to the engine's nitrogen oxide emissions. Since SCR catalysts can store NH ₃ up to a certain limit, the dosage on average must correspond to the NO _x emission. If the dosage is too low, the efficiency of nitrogen oxide reduction decreases, too much urea is added, so the ammonia formed from it can not react with NO _x and get into the environment. Since ammonia has a pungent odor and can already be detected in very small concentrations, this would lead to an odor nuisance in the vicinity of the vehicle in the event of an overdose. A remedy is to install an oxidation catalytic converter behind the SCR catalytic converter. In the case of an ammonia overdose, this converts the NH ₃ back into nitrogen and water. Another way to prevent the so-called ammonia slip, is a larger design of the catalyst in order to obtain a certain memory function.

Thermolysis is a chemical reaction in which a starting material is decomposed by heating it into several products. In contrast to thermal decomposition (= pyrolysis), thermolysis is used specifically for the preparation of defined products or reactive intermediates.

Hydrolysis is the cleavage of chemical compounds with water.

In general:

Thermolysis of urea:

• (NH ₂ ) 2CO → NH ₃ + HNCO (isocyanic acid)

Hydrolysis of the resulting isocyanic acid:

• HNCO + H ₂ O → NH ₃ + CO ₂

Reduction of nitrogen oxides:

• 4NH ₃ + 4NO + O ₂ → 4N ₂ + 6H ₂ O ("Standard SCR") 2NH ₃ + NO + NO ₂ → 2N ₂ + 3H ₂ O ("Fast SCR") 4NH ₃ + 3NO ₂ → 3.5N ₂ + 6H ₂ O ("Slow SCR")

The nitrogen oxide reduction takes place without changing the engine combustion and thus receives the very good efficiency of diesel engines.

List of abbreviations:

• AdBlue

  32.5% aqueous urea solution

  ANB

  exhaust aftertreatment

  ASC

  Ammonia slip catalyst

  CRT

  Continuously Regeneration Trap

  CSF

  Particulate filter with a coating for the oxidation of exhaust gas components

  DOC

  Diesel oxidation catalyst

  DPF

  diesel particulate Filter

  NH3

  ammonia

  NOx

  Sum of nitrogen oxides produced during engine combustion (NO, NO ₂ , N ₂ O, etc.)

  RG

  reaction rate

  SCR

  Selective catalytic reduction

  SDPF

  Diesel particulate filter with SCR active coating

LIST OF REFERENCE NUMBERS

1

Internal combustion engine

2

exhaust gas line

3

Urea aqueous solution tank

5

DOC

6

SDPF

7

SCR

8th

ASC

9

NOx sensor

10

cylinder head

11

double-walled exhaust pipe

12

Flüssigharnförderpumpe

13

Water jacket in the crankcase

14

Heat exchanger, spiral, shell and tube heat exchanger

15

metering

16

mixing section

QUOTES INCLUDE IN THE DESCRIPTION

This list of the documents listed by the applicant has been generated automatically and is included solely for the better information of the reader. The list is not part of the German patent or utility model application. The DPMA assumes no liability for any errors or omissions.

Cited patent literature

• EP 1054722 B [0004, 0014]
• DE 10348800 [0006]
• DE 102007029674 [0007]
• DE 102007042836 [0008]
• DE 102009009538 [0009]
• DE 102007011184 [0010]
• WO 2012/022687 [0011]
• DE 102009025135 [0012]
• DE 102008012087 [0013]
• EP 2177728 A [0017]
• EP 2192279 A [0017]
• WO 2010/139429 [0017]
• DE 102014001879 [0024]
• EP 1054766 B [0042]

Cited non-patent literature

• C. Hagelüken et al, "Auto-Abatement Catalysts, 2nd ed., Expert Verlag 2005, p. 102 [0032]
• DIN 70070 [0051]

Claims (7)

Procedure Cleaning diesel engine exhaust gases with the following process steps: a. Passing the exhaust gas to be purified through a diesel oxidation catalyst (DOC) for the oxidation of gaseous residual hydrocarbons (HC) and of carbon monoxide (CO) to carbon dioxide (CO ₂ ) and for the at least partial oxidation of nitrogen monoxide (NO) contained in the exhaust gas to nitrogen dioxide (NO ₂ ) ; b. Addition of gaseous ammonia (NH ₃ ) to the resulting from step a.) Exhaust gas; c. Passing the exhaust gas resulting from step b.) Through an SCR-catalytically activated particulate filter (SDPF) for reducing the particles contained in the exhaust gas and the nitrogen oxides contained in the exhaust gas; d. Passing the exhaust gas resulting from step c.) Through a selective ammonia oxidation catalyst (ASC) to reduce residual ammonia levels. A method according to claim 1, characterized in that the resulting from step c.) Exhaust gas before being passed through the selective ammonia oxidation catalyst (ASC) in step d.) Initially through a between SCR catalytically activated particulate filter and ASC arranged, additional SCR catalyst is passed , A method according to claim 1, characterized in that the proportion of in step a.) NO ₂ generated in the NO _x in the resulting from step a.) Exhaust gas is more than 50%. Method according to one of claims 1 or 2, characterized in that the SCR catalytically activated particulate filter (SDPF) is operated with a passive regeneration concept. A method according to claim 4, characterized in that the oxidation of the soot particles stored in the SDPF takes place at least proportionally with NO ₂ , which was produced in step a.). A method according to claim 2, characterized in that between the SCR catalytically activated particulate filter and the downstream, additional SCR catalyst is a second metering point, by means of which gaseous ammonia (NH ₃ ) is supplied to the resulting from step c.) Exhaust gas. A method according to claim 6, characterized in that the denitration efficiency of the SCR catalytically activated particulate filter is limited by limiting the amount of gaseous ammonia (NH ₃ ) fed in step b.).

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