US20010053342A1 - Method and device for selective catalytic nox reduction - Google Patents
Method and device for selective catalytic nox reduction Download PDFInfo
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- US20010053342A1 US20010053342A1 US09/254,291 US25429199A US2001053342A1 US 20010053342 A1 US20010053342 A1 US 20010053342A1 US 25429199 A US25429199 A US 25429199A US 2001053342 A1 US2001053342 A1 US 2001053342A1
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- ammonia
- storage medium
- container
- exhaust gas
- heated
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- 238000000034 method Methods 0.000 title claims abstract description 23
- 230000003197 catalytic effect Effects 0.000 title claims abstract 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 99
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 47
- 239000007789 gas Substances 0.000 claims abstract description 18
- 239000003054 catalyst Substances 0.000 claims abstract description 17
- 239000007787 solid Substances 0.000 claims abstract description 15
- 238000010438 heat treatment Methods 0.000 claims abstract description 9
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 4
- 239000001301 oxygen Substances 0.000 claims abstract description 4
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 4
- 239000000126 substance Substances 0.000 claims description 9
- 229910001631 strontium chloride Inorganic materials 0.000 claims description 8
- AHBGXTDRMVNFER-UHFFFAOYSA-L strontium dichloride Chemical compound [Cl-].[Cl-].[Sr+2] AHBGXTDRMVNFER-UHFFFAOYSA-L 0.000 claims description 8
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 4
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 4
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 claims description 3
- 229910001628 calcium chloride Inorganic materials 0.000 claims description 3
- 239000001110 calcium chloride Substances 0.000 claims description 3
- 239000002826 coolant Substances 0.000 claims description 3
- 239000002918 waste heat Substances 0.000 claims description 3
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 2
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 2
- 238000010521 absorption reaction Methods 0.000 claims description 2
- 229910052784 alkaline earth metal Inorganic materials 0.000 claims description 2
- 150000001342 alkaline earth metals Chemical class 0.000 claims description 2
- 150000003841 chloride salts Chemical class 0.000 claims description 2
- 229910017052 cobalt Inorganic materials 0.000 claims description 2
- 239000010941 cobalt Substances 0.000 claims description 2
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims description 2
- 229910052802 copper Inorganic materials 0.000 claims description 2
- 239000010949 copper Substances 0.000 claims description 2
- 238000005485 electric heating Methods 0.000 claims description 2
- 229910052742 iron Inorganic materials 0.000 claims description 2
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims description 2
- 229910052759 nickel Inorganic materials 0.000 claims description 2
- 150000003839 salts Chemical class 0.000 claims description 2
- 150000003467 sulfuric acid derivatives Chemical class 0.000 claims description 2
- 239000011701 zinc Substances 0.000 claims description 2
- 229910052725 zinc Inorganic materials 0.000 claims description 2
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 13
- 239000004202 carbamide Substances 0.000 description 13
- 230000007062 hydrolysis Effects 0.000 description 8
- 238000006460 hydrolysis reaction Methods 0.000 description 8
- 238000006722 reduction reaction Methods 0.000 description 7
- 239000003795 chemical substances by application Substances 0.000 description 5
- 238000010531 catalytic reduction reaction Methods 0.000 description 3
- 230000008014 freezing Effects 0.000 description 3
- 238000007710 freezing Methods 0.000 description 3
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 239000000654 additive Substances 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- VZTDIZULWFCMLS-UHFFFAOYSA-N ammonium formate Chemical compound [NH4+].[O-]C=O VZTDIZULWFCMLS-UHFFFAOYSA-N 0.000 description 1
- 230000002528 anti-freeze Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000002283 diesel fuel Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000012429 reaction media Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 229910001427 strontium ion Inorganic materials 0.000 description 1
- PWYYWQHXAPXYMF-UHFFFAOYSA-N strontium(2+) Chemical compound [Sr+2] PWYYWQHXAPXYMF-UHFFFAOYSA-N 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- WTHDKMILWLGDKL-UHFFFAOYSA-N urea;hydrate Chemical compound O.NC(N)=O WTHDKMILWLGDKL-UHFFFAOYSA-N 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01C—AMMONIA; CYANOGEN; COMPOUNDS THEREOF
- C01C1/00—Ammonia; Compounds thereof
- C01C1/003—Storage or handling of ammonia
- C01C1/006—Storage or handling of ammonia making use of solid ammonia storage materials, e.g. complex ammine salts
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8621—Removing nitrogen compounds
- B01D53/8625—Nitrogen oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion ; Methods of operation or control of catalytic converters
- F01N3/2066—Selective catalytic reduction [SCR]
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/206—Ammonium compounds
- B01D2251/2062—Ammonia
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/02—Adding substances to exhaust gases the substance being ammonia or urea
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/06—Adding substances to exhaust gases the substance being in the gaseous form
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/10—Adding substances to exhaust gases the substance being heated, e.g. by heating tank or supply line of the added substance
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/14—Arrangements for the supply of substances, e.g. conduits
- F01N2610/1406—Storage means for substances, e.g. tanks or reservoirs
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/14—Arrangements for the supply of substances, e.g. conduits
- F01N2610/1446—Means for damping of pressure fluctuations in the delivery system, e.g. by puffer volumes or throttling
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02T—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
- Y02T10/00—Road transport of goods or passengers
- Y02T10/10—Internal combustion engine [ICE] based vehicles
- Y02T10/12—Improving ICE efficiencies
Definitions
- the invention relates to a method and a device for selective catalytic reduction of NOx levels in oxygen-containing exhaust gases using ammonia and a reduction catalyst.
- Ammonia is known as a selective and effective reduction agent for the catalytic reduction (SCR) of nitrogen oxides in oxygen-containing exhaust gases of internal combustion engines, for example.
- European Patent B1 0 487 886 describes a method of quantitative hydrolysis of urea wherein an aqueous urea solution is sprayed onto an evaporator and forwarded via a hydrolysis catalyst with the surfaces of the evaporator and hydrolysis catalyst being coated with active components that catalyze the quantitative hydrolysis of urea into ammonia and CO 2 and inhibit the formation of solid urea reaction products.
- the above-mentioned method has the disadvantage that a liquid must be added for preparing the reaction medium, and this liquid cannot be metered as accurately as a gaseous medium. Therefore, the gas stream that leaves the reduction catalyst usually still contains unreacted ammonia, which cannot be simply released into the atmosphere, but must be decomposed into non-toxic components using an oxidation catalyst.
- the hydrolysis catalyst has the additional disadvantage that it absorbs ammonia at low temperatures. If the temperature rises quickly, most of the absorbed ammonia is released and can no longer be used as a reduction agent for selective catalytic reduction.
- the use of an aqueous urea solution causes other problems—in winter operation of motor vehicles and due to the drop in exhaust gas temperature because of water evaporating in the exhaust gas: the 30%- 35% aqueous urea solution used in the related art has a freezing point of about ⁇ 11° C. At lower temperatures, particularly at the freezing point of diesel fuel, the operation of the motor vehicle is no longer ensured. While the freezing point can be lowered using additives, additives such as ammonium formiate, for example, are usually particularly corrosive, so that their use poses new problems.
- the exhaust gas is cooled by about 20 K due to the need of evaporating the water it contains.
- the unsatisfactory low-temperature performance of SCR catalysts is particularly strongly manifested in this case.
- the method according to the present invention with the features of the main claim has the advantage over the related art that a gaseous reduction agent is provided, which can be accurately metered, causes no problems in winter operation and thus requires no additional antifreeze measures; the problem of poor low-temperature performance of SCR catalysts is thus somewhat alleviated with its use.
- the device for carrying out the method according to the present invention is simple, since no urea hydrolysis catalyst is used, in addition to being compact due to the fact that ammonia in the solid storage medium according to the present invention takes up 3 times less space than the aqueous urea solution. The space thus freed up can possibly be used for an additional SCR unit.
- the solid storage media used according to the present invention are regeneratable, i.e., the emptied container can be refilled with ammonia.
- the number of regeneration cycles may be as high as 1000.
- Strontium chloride SrCl2 which has a high storage density for ammonia, comparable to the storage density of solid urea, can be advantageously used as the solid storage medium.
- Strontium chloride can be replaced totally or in part by calcium chloride, which offers comparable advantages.
- the device according to the present invention can be advantageously equipped with a buffer container for gaseous ammonia in order to have gaseous ammonia available even in intermittent engine operation and/or in start phases, regardless of the heating phase of container 1 , when there is insufficient energy for heating the ammonia storage medium.
- FIG. 1 schematically shows a device according to the present invention
- FIG. 2 shows a specifically adapted embodiment
- FIG. 3 shows an additional specifically adapted embodiment of a device according to the present invention.
- the device of FIG. 1 has a container 1 , which can be heated using a heating device 3 and contains ammonia-storing substance 2 .
- the volume of container 1 is designed so that there is sufficient ammonia available to remove NOx from the exhaust gas of an internal combustion engine with the help of the catalyst system within an interval between servicings of the vehicle. It has been shown that a volume of approximately 10 liters is particularly suitable.
- Substances that store ammonia at ambient conditions (approx. 20° C.) so that the ammonia vapor pressure over the storage medium is low in a closed system ( ⁇ 0.5 bar) can be used as solid storage media.
- the solid storage media according to the present invention may contain substances that bind ammonia by physical and/or chemical absorption, such as active carbon, zeolites, etc., for example.
- Substances that bind ammonia in the form of a chemical complex can also be used as solid storage media. These include, for example, salts, in particular chlorides and/or sulfates of one or more alkaline earth metals and/or of one or more 3d subgroup elements, preferably manganese, iron, cobalt, nickel, copper and/or zinc, can be considered.
- a solid storage medium containing strontium chloride SrCl2 is advantageously used.
- Strontium chloride stores up to eight ammonia molecules per strontium ion, forming [(Sr(NH3)8]Cl2. With an approximate density of 1.5 g/cm 3 , a stored amount of 48 moles NH 3 results per liter of storage medium. In comparison, urea, with a density of 1.32 g/cm 3 , provides storage of 44 moles of ammonia per liter of solid urea.
- Strontium chloride can be replaced totally or in part with calcium chloride.
- An electric heating system and/or a heating device that uses the waste heat of the engine coolant and/or the exhaust gas can be used as heating device 3 .
- the gaseous ammonia formed when the solid storage medium is heated is metered via an electrically or pneumatically actuated valve 4 , controlled by a controller 5 , via ammonia supply line 6 , into the exhaust gas line 8 between engine 7 and catalyst 9 .
- a buffer container 10 is connected between valve 4 and exhaust gas line 8 .
- Buffer container 10 is connected to exhaust gas line 8 via a valve 4 b controlled by controller 5 .
- valves 4 and 4 b are closed, so that buffer container 10 is filled with gaseous ammonia under pressure.
- stored gaseous ammonia can be available even immediately after starting the engine, regardless of the heating phase of container 1 .
- FIG. 3 One system having additional advantageous devices is illustrated in FIG. 3.
- a filling nozzle with integrated check valve 16 which prevents ammonia being supplied from escaping through the filling opening, is provided for filling container 1 .
- a finely porous, sieve-like construction 11 prevents the granulated storage substance 2 in container 1 from being entrained to the outside.
- a pressure sensor 12 is mounted on container 1 for control and safety; it interrupts the supply of heat when a predefined maximum pressure level is attained. Furthermore, a safety valve 13 (opening pressure approx. 10 to 15 bar) is provided, which responds to an excessively steep increase in the storage container pressure and conducts the released ammonia into the exhaust line, for example.
- a pressure limiter 14 which ensures the required ammonia pressure of 2 to 3 bar, is provided downstream from buffer container 10 .
- an ammonia metering station 15 for example, a metering tube with a screen, is provided to guarantee proper mixing of ammonia with the exhaust gas stream.
- An electronic controller in which additional functions adjusting the amount of ammonia to the actual operating state of the engine are implemented, monitors and controls the procedures.
Abstract
Description
- The invention relates to a method and a device for selective catalytic reduction of NOx levels in oxygen-containing exhaust gases using ammonia and a reduction catalyst.
- Ammonia is known as a selective and effective reduction agent for the catalytic reduction (SCR) of nitrogen oxides in oxygen-containing exhaust gases of internal combustion engines, for example.
- For reasons of toxicity and safety problems arising from storing gaseous ammonia, in particular, procedures whereby ammonia is generated at the site of its use as a reduction agent by hydrolysis of urea have been developed.
- European Patent B1 0 487 886 describes a method of quantitative hydrolysis of urea wherein an aqueous urea solution is sprayed onto an evaporator and forwarded via a hydrolysis catalyst with the surfaces of the evaporator and hydrolysis catalyst being coated with active components that catalyze the quantitative hydrolysis of urea into ammonia and CO2 and inhibit the formation of solid urea reaction products.
- The above-mentioned method has the disadvantage that a liquid must be added for preparing the reaction medium, and this liquid cannot be metered as accurately as a gaseous medium. Therefore, the gas stream that leaves the reduction catalyst usually still contains unreacted ammonia, which cannot be simply released into the atmosphere, but must be decomposed into non-toxic components using an oxidation catalyst.
- The procedure is associated with high equipment costs due to the hydrolysis catalyst, as well as the transport of urea and its introduction, which must be uniform over the cross section of the flow.
- The hydrolysis catalyst has the additional disadvantage that it absorbs ammonia at low temperatures. If the temperature rises quickly, most of the absorbed ammonia is released and can no longer be used as a reduction agent for selective catalytic reduction.
- The use of an aqueous urea solution causes other problems—in winter operation of motor vehicles and due to the drop in exhaust gas temperature because of water evaporating in the exhaust gas: the 30%- 35% aqueous urea solution used in the related art has a freezing point of about −11° C. At lower temperatures, particularly at the freezing point of diesel fuel, the operation of the motor vehicle is no longer ensured. While the freezing point can be lowered using additives, additives such as ammonium formiate, for example, are usually particularly corrosive, so that their use poses new problems.
- The exhaust gas is cooled by about 20 K due to the need of evaporating the water it contains. The unsatisfactory low-temperature performance of SCR catalysts is particularly strongly manifested in this case.
- The method according to the present invention with the features of the main claim has the advantage over the related art that a gaseous reduction agent is provided, which can be accurately metered, causes no problems in winter operation and thus requires no additional antifreeze measures; the problem of poor low-temperature performance of SCR catalysts is thus somewhat alleviated with its use.
- In addition, the device for carrying out the method according to the present invention is simple, since no urea hydrolysis catalyst is used, in addition to being compact due to the fact that ammonia in the solid storage medium according to the present invention takes up 3 times less space than the aqueous urea solution. The space thus freed up can possibly be used for an additional SCR unit.
- The requirements for the metering system are less stringent, since, in contrast with a urea-water solution, clogging problems in the metering components cannot occur.
- There is no more need for compressed air support for introducing the reduction agent, since a sufficient pressure gradient with respect to the exhaust system is always created when ammonia is released. The system is therefore equally well suited for use in passenger cars and utility vehicles.
- In contrast with methods using gaseous ammonia, safety problems are alleviated, since the ammonia carried in the vehicle is mostly bound to the storage substance, i.e., it is not freely available.
- Furthermore, it is particularly advantageous that the solid storage media used according to the present invention are regeneratable, i.e., the emptied container can be refilled with ammonia. The number of regeneration cycles may be as high as 1000.
- Advantageous refinements of and improvements on the method described in the main claim are made possible by the measures described in the subclaims.
- Strontium chloride SrCl2, which has a high storage density for ammonia, comparable to the storage density of solid urea, can be advantageously used as the solid storage medium. Strontium chloride can be replaced totally or in part by calcium chloride, which offers comparable advantages.
- It is particularly advantageous to use the waste heat of the engine coolant and/or the exhaust gas to heat the solid storage medium.
- The device according to the present invention can be advantageously equipped with a buffer container for gaseous ammonia in order to have gaseous ammonia available even in intermittent engine operation and/or in start phases, regardless of the heating phase of
container 1, when there is insufficient energy for heating the ammonia storage medium. - The invention is elucidated in the following with reference to the drawings, which illustrate three embodiments of devices intended to carry out the method according to the present invention in a motor vehicle.
- In particular,
- FIG. 1 schematically shows a device according to the present invention;
- FIG. 2 shows a specifically adapted embodiment; and
- FIG. 3 shows an additional specifically adapted embodiment of a device according to the present invention.
- The device of FIG. 1 has a
container 1, which can be heated using aheating device 3 and contains ammonia-storingsubstance 2. - The volume of
container 1 is designed so that there is sufficient ammonia available to remove NOx from the exhaust gas of an internal combustion engine with the help of the catalyst system within an interval between servicings of the vehicle. It has been shown that a volume of approximately 10 liters is particularly suitable. - Substances that store ammonia at ambient conditions (approx. 20° C.) so that the ammonia vapor pressure over the storage medium is low in a closed system (<0.5 bar) can be used as solid storage media.
- The solid storage media according to the present invention may contain substances that bind ammonia by physical and/or chemical absorption, such as active carbon, zeolites, etc., for example.
- Substances that bind ammonia in the form of a chemical complex can also be used as solid storage media. These include, for example, salts, in particular chlorides and/or sulfates of one or more alkaline earth metals and/or of one or more 3d subgroup elements, preferably manganese, iron, cobalt, nickel, copper and/or zinc, can be considered.
- A solid storage medium containing strontium chloride SrCl2 is advantageously used. Strontium chloride stores up to eight ammonia molecules per strontium ion, forming [(Sr(NH3)8]Cl2. With an approximate density of 1.5 g/cm3, a stored amount of 48 moles NH3 results per liter of storage medium. In comparison, urea, with a density of 1.32 g/cm3, provides storage of 44 moles of ammonia per liter of solid urea. Strontium chloride can be replaced totally or in part with calcium chloride.
- In the case of [(Sr(NH3)8]Cl2, perceptible release of ammonia begins at approximately 30° C., resulting in an ammonia vapor pressure of approximately 0.8 bar. At 80° C., the ammonia vapor pressure is about 8 bar. The device should be operated so that the pressure in
container 1 is preferably between 2 and 10 bar. - An electric heating system and/or a heating device that uses the waste heat of the engine coolant and/or the exhaust gas can be used as
heating device 3. - The gaseous ammonia formed when the solid storage medium is heated is metered via an electrically or pneumatically actuated
valve 4, controlled by acontroller 5, viaammonia supply line 6, into theexhaust gas line 8 betweenengine 7 and catalyst 9. - According to a preferred embodiment (FIG. 2), a
buffer container 10 is connected betweenvalve 4 andexhaust gas line 8.Buffer container 10 is connected toexhaust gas line 8 via avalve 4 b controlled bycontroller 5. When the vehicle is turned off,valves buffer container 10 is filled with gaseous ammonia under pressure. Thus, with the device according to FIG. 2, stored gaseous ammonia can be available even immediately after starting the engine, regardless of the heating phase ofcontainer 1. - One system having additional advantageous devices is illustrated in FIG. 3.
- A filling nozzle with integrated
check valve 16, which prevents ammonia being supplied from escaping through the filling opening, is provided forfilling container 1. - A finely porous, sieve-like construction11 prevents the granulated
storage substance 2 incontainer 1 from being entrained to the outside. - A
pressure sensor 12 is mounted oncontainer 1 for control and safety; it interrupts the supply of heat when a predefined maximum pressure level is attained. Furthermore, a safety valve 13 (opening pressure approx. 10 to 15 bar) is provided, which responds to an excessively steep increase in the storage container pressure and conducts the released ammonia into the exhaust line, for example. - A
pressure limiter 14, which ensures the required ammonia pressure of 2 to 3 bar, is provided downstream frombuffer container 10. - At a suitable point upstream from catalyst9, an
ammonia metering station 15, for example, a metering tube with a screen, is provided to guarantee proper mixing of ammonia with the exhaust gas stream. - An electronic controller (Diesel EDC), in which additional functions adjusting the amount of ammonia to the actual operating state of the engine are implemented, monitors and controls the procedures.
Claims (10)
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
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DE19728343.8 | 1997-07-03 | ||
DE19728343 | 1997-07-03 | ||
DE19728343A DE19728343C5 (en) | 1997-07-03 | 1997-07-03 | Process and apparatus for selective catalytic NOx reduction |
PCT/DE1998/001731 WO1999001205A1 (en) | 1997-07-03 | 1998-06-25 | METHOD AND DEVICE FOR SELECTIVE CATALYTIC NOx REDUCTION |
Publications (2)
Publication Number | Publication Date |
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US20010053342A1 true US20010053342A1 (en) | 2001-12-20 |
US6387336B2 US6387336B2 (en) | 2002-05-14 |
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ID=7834467
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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US09/254,291 Expired - Fee Related US6387336B2 (en) | 1997-07-03 | 1998-06-25 | Method and device for selective catalytic NOx reduction |
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US (1) | US6387336B2 (en) |
EP (1) | EP0932440B1 (en) |
JP (2) | JP4873580B2 (en) |
DE (2) | DE19728343C5 (en) |
WO (1) | WO1999001205A1 (en) |
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Also Published As
Publication number | Publication date |
---|---|
WO1999001205A1 (en) | 1999-01-14 |
DE19728343C1 (en) | 1999-04-15 |
JP2012024761A (en) | 2012-02-09 |
DE59807858D1 (en) | 2003-05-15 |
JP5825952B2 (en) | 2015-12-02 |
EP0932440B1 (en) | 2003-04-09 |
JP4873580B2 (en) | 2012-02-08 |
JP2001500063A (en) | 2001-01-09 |
DE19728343C5 (en) | 2013-02-21 |
EP0932440A1 (en) | 1999-08-04 |
US6387336B2 (en) | 2002-05-14 |
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