BACKGROUND OF THE INVENTION
1. Technical Filed
[0001] The present invention relates to an exhaust gas purifier for removing particulate
matters in exhaust gas discharged from an internal combustion engine.
2. Description of the Related Art
[0002] In an internal combustion engine that is mounted on an automobile or the like, it
is required to purify harmful gas components such as nitrogen oxide (NOx) and hydrocarbon
(HC) contained in exhaust gas to improve exhaust emission. In particular, in the case
of a diesel engine, it is important to decrease so-called particulate matters (PM)
such as soot and SOF (Soluble Organic Fraction) in addition to nitrogen oxide and
hydrocarbon.
[0003] In order to cope with such a requirement, "an exhaust gas purifier for an internal
combustion engine" as described in Japanese Patent No. 2722987 was proposed in the
past. The exhaust gas purifier for an internal combustion engine described in the
patent is provided with a particulate filter for collecting particulate matters in
exhaust gas in an exhaust passageway of an internal combustion engine and has an NOx
absorbent, which absorbs NOx in exhaust gas when an air-fuel ratio of the exhaust
gas is lean and emits and reduces absorbed NOx when an oxygen concentration in exhaust
gas is low and an absorbent exists, disposed in a position where the NOx absorbent
can transfer heat to and from the particulate filter.
[0004] With such a configuration, the exhaust gas purifier for an internal combustion engine
causes temperature of the particulate filter to rise utilizing heat generated when
a reducer burns on the NOx absorbent to thereby burn and remove the particulate matters
collected in the particulate filter.
[0005] On the other hand, when a particulate filter is used, an exhaust channel in the particulate
filter is blocked by concentration of a compound called ash and thus a pressure loss
of exhaust gas increases.
[0006] Although a mechanism for generating ash has not been clarified, it is presumed that
various additives and impurities contained in fuel and lubricating oil of an internal
combustion engine combine with each other in a combustion chamber of the internal
combustion engine or on the particulate filter, to thereby form various compounds
which concentrate on the particulate filter to generate ash.
[0007] For example, components such as sulfur (S) , phosphorous (P) , calcium (Ca) and magnesium
(Mg) are contained in fuel and lubricating oil of an internal combustion engine, and
components contained in blow-by gas (lubricating oil) and components contained in
air-fuel mixture combine in a combustion chamber to generate compounds such as calcium
sulfate (CaSO
4), calcium phosphate (Ca
3(PO
4)
2) and magnesium sulfate (MgSO
4), which are collected on a particulate filter together with particulate matters (PM)
to concentrate as ash.
[0008] In addition, since sulfur (S) has a characteristic that it is easily absorbed in
soot, sulfur (S) absorbed in a particulate filter together with soot combines with
calcium (Ca) and magnesium (Mg) in exhaust gas to generate compounds such as calcium
sulfate (CaSO
4) and magnesium sulfate (MgSO
4), which concentrate as ash.
[0009] In order to cope with this problem, Japanese Patent Application Laid-open No. 2001-12229
discloses an exhaust gas purifier for an internal combustion engine, which is provided
with a collecting material for collecting particulate matters, the collecting material
having loaded therewith a metal having an electronegativity equal to or lower than
that of a predetermined component contained in fuel and/or lubricating oil of an internal
combustion engine.
[0010] In this way, the collecting material is loaded with the metal having an electronegativity
equal to or lower than a predetermined component contained in lubricant, preferably
a metal having an electronegativity lower than that of the predetermined component
and strong ionization tendency. As a result, since a component to be combined combines
with the metal rather than with the predetermined component, formation of the ash
is inhibited.
[0011] However, it has been found that, even if the collecting material is used, it is difficult
to prevent plugging of a particulate filter by calcium phosphate (Ca
3(PO
4)
2) as an ash component.
[0012] This is because, although phosphorous P and sulfur S do not usually combine with
each other, calcium Ca that most easily combines with phosphorous P is contained as
calcium sulfate (CaSO
4) as described above, whereby phosphorous P and sulfur S concentrate in the particulate
filter to be collected therein. Then, plugging by calcium phosphate (Ca
3(PO
4)
2) occurs in the particulate filter.
[0013] In particular, when a vehicle continuously runs in a region of that temperature of
exhaust gas becomes high, a needle-like crystal of calcium phosphate (Ca
3(PO
4)
2) is formed on a surface of a particulate filter loading with a noble metal such as
platinum (Pt) and having a catalytic function, whereby a space is generated between
purified matters and the noble metal, and the catalytic function may be down by half
or lifetime of a catalyst may be shorten.
SUMMARY OF THE INVENTION
[0014] The present invention has been devised in view of the above-mentioned circumstance
and it is an object of the present invention to provide a technology capable of inhibiting
generation of ash, in particular, generation of ash due to calcium phosphate (Ca
3(PO
4)
2), in an exhaust gas purifier provided with a collecting material for collecting particulate
matters contained in exhaust gas that is discharged from an internal combustion engine.
[0015] The present invention adopts the following measures in order to solve the above problem.
[0016] That is, the exhaust gas purifier for an internal combustion engine according to
the present invention is characterized in that, in an exhaust gas purifier for an
internal combustion engine which is provided with a collecting material for collecting
particulate matters contained in exhaust discharged from the internal combustion engine,
an ash trap for absorbing phosphorous (P) in exhaust gas is provided upstream of the
collecting material.
[0017] In the exhaust gas purifier configured as described above, the collecting material
collects particulate matters contained in exhaust gas discharged from the internal
combustion engine. The term of the collecting material here may be, for example, an
ordinary DPF (Diesel Particulate Filter) for collecting particulate matters or a DPF
loaded with a catalytic substance such as a NOx absorbent.
[0018] In addition, it is likely that components originally contained in fuel and/or lubricating
oil of the internal combustion engine exist in the exhaust gas. Therefore, there are
possibility that a given components of those components may combine with another component
(hereinafter referred to as a combined component) on the collecting material to form
ash. However, if the ash trap is provided upstream of the collecting material, since
the phosphor (P) is absorbed by the ash trap, formation of ash can be restrained by
the collecting material provided downstream of the ash trap.
[0019] This ash trap may be loaded with a basic metal with strong ionization tendency. In
this way, it becomes possible to steadily absorb phosphorous (P) in the form of calcium
phosphate (Ca
3(PO
4)
2) or the like.
[0020] The term of the basic metal here means a metal having an electronegativity such as
lithium (Li), sodium (Na), potassium (K) , rubidium (Rb), cesium (Cs), francium (Fr),
beryllium (Be), magnesium (Mg), calcium (Ca), strontium (Sr), barium (Ba), radium
(Ra) and lanthanum (La), preferably a metal having an electronegativity lower than
that of the predetermined component and having strong ionization tendency. Since phosphorous
P steadily combines with these metals, formation of ash by calcium phosphate (Ca
3(PO
4)
2) in the collecting material downstream of the ash trap is inhibited.
[0021] In addition, it is preferable to load the collecting material with a metal having
an electronegativity equal to or lower than a predetermined component contained in
fuel or lubricant oil of the internal combustion engine. In this way, it is possible
to restrain the concentration on the collecting material as ash consisting of a compound
such as calcium sulfate (CaSO
4) and magnesium sulfate (MgSO
4) which combined sulfur (S) with calcium (Ca) and magnesium (Mg) in exhaust gas.
[0022] Further, since it is likely that the compounds of the metal loaded on the collecting
material and the predetermined component such as sulfur concentrate on the collecting
material in the same manner as the ash does, it is preferable to select the metal
to be loaded such that these compounds are decomposed or removed under the same conditions
as purifying conditions of particulate matters.
[0023] In addition, the ash trap may be imparted with an oxidation performance. If the oxidation
performance is imparted, since concentration of calcium phosphate (Ca
3(PO
4)
2) that is formed by phosphorous and calcium combining with each other is facilitated,
it becomes easy to trap phosphorous here.
[0024] According to the present invention, in order to prevent phosphorous in exhaust gas
from being combined with calcium and being concentrated on a collecting material to
form ash, an ash trap loaded with a basic metal having an electronegativity that would
facilitate combining thereof with phosphorous is provided in a pre-stage of this collecting
material so that phosphor is absorbed by this ash trap. Thus, it is possible to inhibit
ash from being formed by calcium phosphate (Ca
3(PO
4)
2) in the collecting material.
[0025] Other objects and features of the present invention will be apparent from the following
descriptions taken in conjunction with the accompanying drawings, in which like reference
characters designate the same or similar parts throughout the figures thereof.
BRIEF DESCRIPTION OF THE DRAWINGS
[0026] In the accompanying drawings:
Fig. 1 illustrates a schematic configuration of an internal combustion engine to which
an exhaust gas purifier in accordance with the present invention is applied;
Fig. 2 illustrates an exhaust gas purifier mounted with a particulate filter;
Fig. 3A is an image view showing a state in which particulates deposit on a filter
base material;
Fig. 3B is an image view showing a state in which particulates are disturbed by forward
flow and back flow of exhaust gas;
Fig. 4A is a front view of a particulate filter;
Fig. 4B is a side sectional view of the particulate filter; and
Figs. 5A and 5B are a conceptual view showing an oxidation action of particulates.
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS
[0027] An exhaust gas purifier in accordance with the present invention will be described
based on the drawings. In this description, an embodiment in which the exhaust gas
purifier in accordance with the present invention is applied to a diesel engine for
a vehicle will be described.
[0028] Referring to Fig. 1, reference numeral 1 denotes an engine main body, 2 denotes a
cylinder block, 3 denotes a cylinder head, 4 denotes a piston, 5 denotes a combustion
chamber, 6 denotes an electrically-controlled fuel injection valve, 7 denotes an intake
valve, 8 denotes an intake port, 9 denotes an exhaust valve and 10 denotes an exhaust
port. The intake port 8 is coupled to a surge tank 12 via an intake branch pipe 11
and the surge tank 12 is coupled to a compressor 15 of an exhaust turbocharger 14
via an intake duct 13. A throttle valve 17 driven by a step motor 16 is disposed in
the intake duct 13 and a cooling device 18 for cooling intake air flowing in the intake
duct 13 is disposed around the intake duct 13. In an example shown in Fig. 1, engine
cooling water is guided into the cooling device 18 and the intake air is cooled by
the engine cooling water.
[0029] On the other hand, the exhaust port 10 is coupled to an exhaust turbine 21 of the
exhaust turbocharger 14 via an exhaust manifold 19 and an exhaust pipe 20. The outlet
of the exhaust turbine 21 is coupled to an exhaust gas purifier having a casing 23
incorporating a particulate filter 22.
[0030] The exhaust manifold 19 and the surge tank 12 are coupled with each other via an
exhaust gas re-circulation (hereinafter referred to as EGR) passageway 24 and an electrically-controlled
EGR control valve 25 is disposed in the EGR passageway 24. In addition, a cooling
device 26 for cooling EGR gas flowing in the EGR passageway 24 is disposed around
the EGR passageway 24. In the example shown in Fig. 1, the engine cooling water is
guided into the cooling device 26 and the EGR gas is cooled by the engine cooling
water.
[0031] On the other hand, each fuel injection valve 6 is coupled to a fuel reservoir, a
so-called common-rail 27, via a fuel supply pipe 6a. Fuel is supplied into the common-rail
27 from an electrically-controlled fuel pump 28 that can change a discharge amount.
The fuel supplied to the common-rail 27 is supplied to the fuel injection valve 6
via each fuel supply pipe 6a. A fuel pressure sensor 29 for detecting a fuel pressure
in the common-rail 27 is attached to the common-rail 27. A fuel discharge amount by
the fuel pump 28 is controlled such that the fuel pressure in the common-rail 27 becomes
equal to a target fuel pressure, based on an output signal of the fuel pressure sensor
29.
[0032] An electronic control unit 30 consists of a digital computer and is provided with
an ROM (Read Only Memory) 32, an RAM (Random Access Memory) 33, a CPU (microprocessor)
34, an input port 35 and an output port 36, which are connected with each other by
a bidirectional bus 31. An output signal of the fuel pressure sensor 29 is inputted
in an input port 35 via an corresponding AD converter 37. In addition, a floor temperature
sensor 39 for detecting a floor temperature of the particulate filter 22 is attached
to the particulate filter 22. An output signal of the floor temperature sensor 39
is inputted in the input port 35 via the corresponding AD converter 37.
[0033] In addition, a load sensor 41 for generating an output voltage proportional to an
amount of stepping L on an accelerator pedal 40 is connected to the accelerator pedal
40 and an output voltage of the load sensor 41 is inputted in the input port 35 via
the corresponding converter 37. Moreover, a crank angle sensor 42 for generating an
output pulse each time a crank shaft rotates by, for example, 30°, is connected to
the input port 35. On the other hand, the output port 36 is connected to the fuel
injection valve 6, the step motor 16 for driving a throttle valve, the EGR control
valve 25, the fuel pump 28 and an actuator 72 discussed below via a corresponding
driving circuit 38.
<Structure of the exhaust gas purifier>
[0034] As shown in Figs. 1 and 2, in the exhaust gas purifier, an exhaust pipe 70 is connected
to the outlet of the exhaust turbine 21. The exhaust gas purifier is provided with
a first exhaust passageway 76 and a second exhaust passageway 77 which branch from
the exhaust pipe 70 to be respectively connected to one side and the other side of
the filter 22 in the casing 23 incorporating the particulate filter 22. Moreover,
the exhaust gas purifier is provided with a bypass passageway 73 for discharging exhaust
gas directly without passing the exhaust gas through the particulate filter 22 from
the branch point of the first exhaust passageway 76 and the second exhaust passageway
77.
[0035] In addition, an exhaust switching valve 71 is provided in the branch point of the
first exhaust passageway 76 and the second exhaust passageway 77. The exhaust switching
valve 71 is driven by the actuator 72 and alternately switches between first flow
(forward flow) in which the first exhaust passageway 76 is selected to flow exhaust
gas from one side of the filter 22 and second flow (back flow) in which the second
exhaust passageway 77 is selected to flow exhaust gas from the other side of the filter
22.
[0036] Further, ash traps 80 and 81 are respectively provided in a pre-stage of the particulate
filter 22 in the first exhaust passageway 76 and the second exhaust passageway 77.
The ash traps 80 and 81 are loaded with basic metal with strong ionization tendency
and phosphorous (P) in exhaust gas is absorbed by the basic metal.
[0037] The basic metal in this context includes, for example, one of lithium (Li), sodium
(Na), potassium (K) , rubidium (Rb), cesium (Cs), francium (Fr), beryllium (Be) ,
magnesium (Mg), calcium (Ca), strontium (Sr), barium (Ba), radium (Ra) and lanthanum
(La) or a combination of two or more of these.
[0038] Moreover, a fuel adding nozzle 83 as reducer adding means for injecting fuel into
exhaust gas flowing into the filter 22 is provided in the first exhaust passageway
77. The fuel-adding nozzle 83 is controlled by controlling means that is realized
on the CPU 34 of the electronic control unit 30.
[0039] Here, the casing 23 for accommodating the filter 22 is disposed in a position right
above the exhaust pipe 70 forming the bypass passageway 73. The first exhaust passageway
76 and the second exhaust passageway 77 branching from the exhaust pipe 70 are connected
to both sides of the casing 23. In addition, provided that a passing direction of
exhaust gas is a length direction, in the filter 22 in the casing 23 a length in a
width direction perpendicular to the length direction is longer than a length in the
length direction. With such a configuration, a space for mounting the exhaust gas
purifier consisting of the casing 23 enclosing the filter 22 can be reduced.
[0040] On the other hand, the actuator 72 is driven to be controlled by controlling means
75 realized on the CPU 34 of the electronic control unit 30 and is driven by a control
signal from the output port 36. In addition, the actuator 72 is driven by a negative
pressure that is formed with driving of the internal combustion engine. The actuator
72 controls a valve body into a position for selecting the first exhaust passageway
76 (forward flow position) when a negative pressure is not applied, controls the valve
body into a neutral position when a first negative pressure is applied and controls
the valve body into a position for selecting the second exhaust passageway 77 (back
flow position) when a second negative pressure stronger than the first negative pressure
is applied.
[0041] When the valve body is in the forward flow position indicated by broken lines of
Fig. 2, the exhaust switching valve 71 connects the exhaust pipe 70 to the first exhaust
passageway 76 and, at the same time, connects the second exhaust passageway 77 to
the bypass passageway 73. Therefore, exhaust gas flows in the order of the exhaust
pipe 70, the first exhaust passageway 76, the filter 22, the second exhaust passageway
77 and the bypass passageway 73 to be released to the atmosphere.
[0042] When the valve body in the back flow position indicated by a solid line of Fig. 2,
the exhaust switching valve 71 connects the exhaust pipe 70 to the second exhaust
passageway 77 and, at the same time, connects the first exhaust passageway 76 to the
bypass passageway 73. Therefore, exhaust gas flows in the order of exhaust pipe 70,
the second exhaust passageway 77, the filter 22, the first exhaust passageway 76 and
the bypass passageway 73 to be released to the atmosphere.
[0043] When the valve body is in the neutral position that is in parallel with the axis
of the exhaust pipe 70 as indicated by alternate long and short dash lines of Fig.
2, the exhaust switching valve 71 connects the exhaust pipe 70 directly to the bypass
passageway 73. Therefore, exhaust gas flows from the exhaust pipe 70 to the bypass
passageway 73 without passing through the filter 22 to be released to the atmosphere.
[0044] Switching between the forward flow and the back flow is repeated by the switching
of the valve body, whereby particulates such as soot move around in the base material
of the filter 22. Therefore, oxidation of the particulates is facilitated and, as
a result, purification of the particulates can be performed efficiently.
[0045] Fig 3A is an image view in the case where exhaust gas is flown through the filter
22 only in one direction. In this case, since particulates accumulate only on one
side of the filter and do not move, particles not only causes increase of a pressure
loss of exhaust gas but also hinders purification of the particulates.
[0046] Fig. 3B is an image view in the case where exhaust gas is flown through the filter
22 in the both directions. In this case, since particulates are disturbed in the forward
flow direction and the back flow direction on both the sides of the filter, the particulates
move around on both the side of the filter 22 or in the base material, whereby oxidation
of the particulates can be facilitated utilizing active sites existing all over the
filter base material and accumulation of the particulates on the filter 22 can be
further decreased. Thus, increase of a pressure loss of exhaust gas can be avoided.
<Structure of the ash trap>
[0047] Although a shape and a structure of each of the ash traps 80 and 81 are not specifically
limited as long as they can collect particulates, if possible, the ash traps with
a large surface area is preferable.
[0048] For example, the ash traps 80 and 81 may be a so-called "wall flow type" which forms
a honeycomb structure, in which a porous substance is used as a base material, and
in which are alternately arranged, in a honeycomb form, first flow paths with end
portions on their upstream sides opened and end portions on their downstream sides
blocked, and second flow paths with end portions on their upstream sides blocked and
end portions on their downstream sides opened. The first flow paths become exhaust
gas inflow passageways with their downstream ends blocked by plugs and the second
flow paths become exhaust gas outflow passageways with their upstream ends blocked
by plugs. These passageways are alternately disposed through thin partitions.
[0049] Phosphorous (P) in exhaust gas is absorbed in the ash traps 80 and 81. In practice,
phosphorous (P) combines with calcium (Ca) and concentrates in the ash traps 80 and
81 in the form of calcium phosphate (Ca
3(PO
4)
2). Therefore, in the particulates filter 22 provided downstream of the ash traps 80
and 81, the formation of ash by calcium phosphate (Ca
3(PO
4)
2) which is combined phosphorous (P) with calcium (Ca) is restrained.
[0050] Alternatively, the ash traps 80 and 81 may be provided in a pre-stage of a switching
flow path, that is, in a pre-stage of the exhaust switching valve 71. Further, phosphorous
(P) in exhaust gas can be trapped doubly by providing the ash traps also in a pre-stage
of the exhaust turbocharger 14. That is, the ash traps exist in both a position close
to an exhaust manifold where temperature is high and a position in the first exhaust
passageway 76 or the second exhaust passageway 77. Therefore, since they can absorb
phosphorous (P) respectively in areas with extremely large temperature difference
from each other, trap efficiency is improved.
<Structure of the filter>
[0051] Fig. 4 shows a structure of the particulate filter 22. Fig. 4A shows a front view
of the particulate filter 22 and Fig. 4B shows a side sectional view of the particulate
filter 22. As shown in Figs. 4A and 4B, the particulate filter 22 forms a honeycomb
structure and is of a so-called "wall flow type" provided with a plurality of exhaust
flow passageways 50 and 51 extending in parallel with each other. These exhaust flow
passageways are constituted by the exhaust gas inflow passageways 50 with their downstream
ends blocked by plugs 52 and the exhaust gas outflow passageways 51 with their upstream
ends blocked by plugs 53. Further, portions with hatching in Fig. 4A indicate the
plugs 53. Therefore, the exhaust gas inflow passageways 50 and the exhaust gas outflow
passageways 51 are alternately disposed through thin partitions 54. In other words,
the exhaust gas inflow passageways 50 and the exhaust gas outflow passageways 51 are
arranged such that each exhaust gas inflow passageway 50 is surrounded by four exhaust
gas outflow passageways 51 and each exhaust gas outflow passageway 51 is surrounded
by four exhaust gas inflow passageways 50.
[0052] The particulate filter 22 is formed of a porous material such as a cordierite. Therefore,
exhaust gas that has flown into the exhaust gas inflow passageways 50 flows out into
the adjoining exhaust gas outflow passageways 51 by passing through the partitions
54 around them as indicated by arrows in Fig. 4B.
[0053] In the embodiment in accordance with the present invention, layers of a carrier made
of, for example, aluminum are formed on circumferential wall surfaces of each exhaust
gas inflow passageway 50 and each exhaust gas outflow passageway 51, that is, on both
side surfaces of each partition 54 and on internal wall surfaces of pores in the partition
54. Loaded on this carrier are a noble metal catalyst and an active oxygen releaser
for taking in and holding oxygen when excessive oxygen exists around it and releasing
the held oxygen in the form of active oxygen when an oxygen concentration falls around
it.
[0054] Platinum (Pt) can be used as the noble metal catalyst. In addition, the active oxygen
releaser can be constituted by at least one metal selected out of: an alkali metal
such as potassium (K), sodium (Na), lithium (Li), cesium (Cs) and rubidium (Rb); an
alkali-earth metal such as barium (Ba), calcium (Ca) and strontium (Sr) ; a rare-earth
such as lanthanum (La) and yttrium (Y); and a transition metal such as cerium (Ce).
[0055] Further, a valence number of the transition metal (oxygen absorbing agent) such as
cerium (Ce) changes according to an oxygen concentration. Thus, active oxygen is released
at a large amount by repeating change in an oxygen concentration as follows.

[0056] In addition, it is preferable to use an alkali metal or an alkali-earth metal having
higher ionization tendency than that of calcium (Ca), that is, potassium (K), lithium
(Li), cesium (Cs), rubidium (Rb), barium (Ba) and strontium (Sr), as the active oxygen
releaser.
[0057] In this embodiment, description will be made with the case in which platinum (Pt)
is loaded as the noble metal catalyst and potassium (K) is loaded as the active oxygen
releaser, on a carrier formed of aluminum or the like as an example.
<Continuous oxidation treatment of particulates by the filter>
[0058] Next, an action for removing particulates in exhaust gas by the particulate filter
22 will be described. Further, the action for removing particulates is also performed
in the same mechanism even when using other alkali metals, alkali-earth metals, rare-earth
or transition metals as the active oxygen releaser.
[0059] In a compression ignition internal combustion engine as shown in Fig. 1, combustion
is performed under a condition of excessive air ratio and, therefore, exhaust gas
contains a large amount of excessive air. That is, an air-fuel ratio of the exhaust
gas is lean in the compression ignition internal combustion engine as shown in Fig.
1. In addition, since nitrogen monoxide (NO) is generated in the combustion chamber
5, nitrogen monoxide (NO) is contained in the exhaust gas. Further, sulfur (S) is
contained in fuel and the sulfur (S) reacts with oxygen in the combustion chamber
5 to be sulfur dioxide (SO
2). Therefore, sulfur dioxide (SO
2) is contained in the exhaust gas. Therefore, the exhaust gas containing excessive
oxygen, nitrogen monoxide (NO) and sulfur dioxide (SO
2) flows into the exhaust gas inflow passageway 50.
[0060] Figs. 5A and 5B schematically show enlarged views of the inner circumference surface
of the exhaust gas inflow passageway 50 and a surface of a carrier layer formed on
the pore inner wall surface within the partition 54. Further, in Figs. 5A and 5B,
reference numeral 60 denotes particles of platinum (Pt) and 61 denotes an active oxygen
releaser containing potassium (K).
[0061] As described above, since a large amount of excessive oxygen is contained in exhaust
gas, when the exhaust gas flows into the exhaust gas inflow passageways 50 of the
particulate filter 22, the oxygen (O
2) deposits on the surface of the platinum (Pt) in the form of O
2- or O
2- as shown in Fig. 5A. On the other hand, nitrogen monoxide (NO) in the exhaust gas
reacts with the O
2- or O
2- on the surface of the platinum (Pt) to become nitrogen dioxide NO
2 (2NO+O
2 → 2NO
2). Subsequently, a part of the generated nitrogen dioxide (NO
2) is absorbed in the active oxygen releaser 61 while being oxidized on the platinum
(Pt) and diffuses in the active oxygen releaser 61 in the form of nitrogen oxide ion
(NO
3-) as shown in Fig. 5A while combining with potassium (K) . A part of the nitrogen
oxide ion (NO
3-) generates potassium nitrate (KNO
3).
[0062] On the other hand, sulfur dioxide (SO
2) is also contained in the exhaust gas as described above and this sulfur dioxide
(SO
2) is also absorbed in the active oxygen releaser 61 by the same mechanism as that
for absorbing nitrogen dioxide (NO). That is, oxygen (O
2) deposits on the surface of the platinum (Pt) in the form of O
2- or O
2- as described above and the SO
2 in the exhaust gas reacts with the O
2- or O
2- on the surface of the platinum (Pt) to become (SO
3).
[0063] Subsequently, a part of the generated (SO
3) is absorbed in the active oxygen releaser 61 while being further oxidized on the
platinum (Pt) and diffuses in the active oxygen releaser 61 in the form of sulfate
oxide ion (SO
42-) while combining with potassium K to generate potassium sulfate (K
2SO
4). In this way, potassium nitrate (KNO
3) and potassium sulfate (K
2SO
4) are generated in the active oxygen releaser 61.
[0064] On the other hand, particulates consisting mainly of carbon C are generated in the
combustion chamber 5. Therefore, these particulates are contained in exhaust gas.
These particulates contained in the exhaust gas contacts and deposits on a surface
of a carrier layer, for example, the surface of the active oxygen releaser 61 as indicated
by reference numeral 62 in Fig. 5B, when the exhaust gas is flowing through the exhaust
gas inflow passageways 50 of the particulate filter 22 or when the exhaust gas moves
from the exhaust gas inflow passageway 50 to the exhaust gas outflow passageway 51.
[0065] When the particulate 62 deposits on the surface of the active oxygen releaser 61
in this way, an oxygen concentration falls on a contact surface between the particulate
62 and the active oxygen releaser 61. When the oxygen concentration thus falls, a
concentration difference occurs between the contact surface and a high oxygen concentration
in the active oxygen releaser 61, whereby oxygen in the active oxygen releaser 61
tends to move to the contact surface between the particulate 62 and the active oxygen
releaser 61. As a result, potassium nitrate (KNO
3) formed in the active oxygen releaser 61 is decomposed into potassium (K) and oxygen
(O). The oxygen (O) moves to the contact surface between the particulate 62 and the
active oxygen releaser 61, and the nitrogen monoxide (NO) is released to the outside
from the active oxygen releaser 61. The nitrogen monoxide (NO) released to the outside
is oxidized on platinum (Pt) on its downstream side and absorbed in the active oxygen
releaser 61 again.
[0066] In addition, it is appeared that active oxygen is also generated in a reaction process
with oxygen and oxidize the particulate 62, when oxygen and NOx in exhaust gas are
occluded in an oxygen-excessive state. Although a detailed mechanism for this phenomenon
is unclear, it is generally assumed as follows.
[0067] As described above, NO in exhaust gas reacts with O
2- or O
2- on the surface of platinum Pt to become NO
2 (2NO+O
2 → 2NO
2). Subsequently, a part of the generated (NO
2) turns into (NO
3) and is absorbed in the active oxygen releaser 61 while being oxidized on platinum
(Pt).
[0068] A part of the NO
2 is decomposed by a catalyst and release active oxygen. That is, the NO
2 repeats oxidation and decomposition in such as follows to release active oxygen;

[0069] On the other hand, at this point, potassium sulfate (K
2SO
4) formed in the active oxygen releaser 61 is also decomposed into potassium K, oxygen
(O) and (SO
2). The oxygen (O) moves to the contact surface between the particulate 62 and the
active oxygen releaser 61 and the SO
2 is released to the outside from the active oxygen releaser 61. The (SO
2) released to the outside is oxidized on platinum (Pt) on its downstream side and
absorbed in the active oxygen releaser 61 again. However, since potassium sulfate
(K
2SO
4) is stable, it is hard to release active oxygen compared with potassium nitrate (KNO
3).
[0070] The Oxygen (O) moving to the contact surface between the particulate 62 and the active
oxygen releaser 61 is oxygen decomposed from compounds such as potassium nitrate (KNO
3) or potassium sulfate (K
2SO
4). The oxygen (O) decomposed from a compound has high energy and has extremely high
activity. Therefore, the oxygen moving to the contact surface between the particulate
62 and the active oxygen releaser 61 has turned into active oxygen (O). When such
active oxygen (O) contacts the particulate 62, the particulate 62 is oxidized in a
short time (within a few minutes to several tens of minutes) without emitting luminous
flames and completely disappears. Therefore, the particulate 62 never deposits on
the particulate filter 22.
[0071] When particulates that deposit on the particulate filter 22 in a laminated shape
is burned in the conventional art, the particulate filter 22 glows and burns accompanied
with flames. Such burning accompanied with flames does not continue unless it is under
a high temperature. Therefore, temperature of the particulate filter 22 must be maintained
high in order to cause the burning accompanied with flames to continue.
[0072] To the contrary, in the present invention, the particulate 62 is oxidized without
emitting luminous flames as described above, when the surface of the particulate filter
22 does not glow. That is, in other words, in the present invention, the particulate
62 is oxidized and removed at a considerably low temperature compared with the conventional
art. Therefore, a particulate removing action by oxidation of the particulate 62 without
emission of luminous flames according to the present invention is completely different
from a particulate removing action by burning of the conventional art that is accompanied
with flames.
[0073] In addition, the particulate removing action by oxidation of particulates is performed
at a considerably low temperature. Therefore, the temperature of the particulate filter
22 does not rise so high, whereby there is almost no risk of the particulate filter
22 deteriorating.
[0074] Moreover, since particulates hardly deposit on the particulate filter 22, a risk
of that concentration of ash which is cinder of particulates is lower. Therefore,
a risk of clogging the particulate filter 22 being becomes lower.
[0075] Incidentally, the clogging is caused mainly by calcium sulfate (CaSO
4). That is, fuel and lubricating oil contain calcium (Ca) and, therefore, calcium
(Ca) is contained in exhaust gas. If SO3 exists, the calcium (Ca) generates calcium
sulfate (CaSO
4). Calcium sulfate (CaSO
4) is solid and is not thermally decomposed even if it is heated. Therefore, when calcium
sulfate (CaSO
4) is generated and the pores of the particulate filter 22 are blocked by the calcium
sulfate (CaSO
4), the clogging is caused.
[0076] However, in this case, if an alkali metal or an alkali-earth metal having ionization
tendency higher than that of calcium (Ca), for example, potassium (K) is used as the
active oxygen releaser 61, SO
3 dispersed in the active oxygen releaser 61 combines with potassium (K) to form potassium
sulfate (K
2SO
4). Calcium (Ca) flows out into the exhaust gas outflow passageways 51 through the
partitions 54 of the particulate filter 22 without combining with SO
3. As a result, the pores of the particulate filter 22 are not clogged any more. Therefore,
it is preferable to use an alkali metal or an alkali-earth metal having ionization
tendency higher than that of calcium (Ca), that is, potassium (K), lithium (Li), cesium
(Cs) or barium (Ba) as the active oxygen releaser 61 as described above.
[0077] Moreover, since potassium sulfate (K
2SO
4) formed on the particulate filter 22 instead of ash has a low concentration compared
with calcium sulfate (CaSO
4), it can be easily decomposed and removed by raising an atmospheric temperature of
the particulate filter 22 or by placing the particulate filter 22 under a reducing
atmosphere.
[0078] Incidentally, in practice, it is almost impossible to reduce an amount of discharged
particulates M to be less than an amount of particulates that can be oxidized and
removed G in all operation states. For example, a temperature of the particulate filter
22 is usually low at the start of an engine. Therefore, the amount of discharged particulates
M is usually greater than the amount of particulates that can be oxidized and removed
G in this case. When the amount of discharged particulates M becomes greater than
the amount of particulates that can be oxidized and removed G as immediately after
the start of an engine, particulates that were not oxidized starts to remain on the
particulate filter 22.
[0079] In this way, the amount of discharged particulates M is increased to be greater than
the amount of particulates that can be oxidized and removed G, and particulates may
deposit on the particulate filter 22 in a laminated shape in some cases.
[0080] In order to oxidize and remove the particulates that deposit on the particulate filter
22, the switching valve 71 disposed in the exhaust pipe 70 is switched. When the switching
valve 71 is switched, the exhaust upstream side and the exhaust downstream side of
the particulate filter 22 are reversed. In a part that was the exhaust downstream
side of the particulate filter 22 before switching the switching valve 71, particulates
deposit on the surface of the active oxygen releaser 61 and active oxygen (O) is released,
whereby the particulates are oxidized and removed. A part of the released active oxygen
O moves to the exhaust downstream side of the particulate filter 22 together with
exhaust gas and oxidize and remove particulates that deposit there. Here, as described
above, the particulates are disturbed in the forward flow direction and the back flow
direction on both the side of the particulate filter 22 and move around on both the
sides of the particulate filter 22 or inside the base material to meet activated points
all over the film base material to be oxidized.
[0081] In this way, when particulate that was not oxidized start to deposit on the particulate
filter 22, particulates can be completely oxidized and removed from the particulate
filter 22 by reversing the exhaust upstream side and the exhaust downstream side of
the particulate filter 22.
[0082] In addition, if particulates deposit on the particulate filter 22, the particulates
is oxidized without emitting luminous flames by causing an air-fuel ratio of a part
of or entire exhaust gas to be rich temporarily. When the air-fuel ratio of the exhaust
gas is made rich, that is, when an oxygen concentration in the exhaust gas is decreased,
active oxygen (O) is released to the outside from the active oxygen releaser 61 without
interruption. The particulates that deposit on the particulate filter 22 is burnt
and removed in a short time (within a few minutes to several tens of minutes) without
emitting luminous flames.
(Other embodiments)
[0083] Although a collecting material is described as a material capable of purifying NOx
and oxidizing particulates in the above-mentioned embodiment, it is not limited to
the above-mentioned one and any material can be adopted as long as it is a filter
for collecting particulate matters such as soot and unburnt fuel components in exhaust
gas.
[0084] In addition, a dummy converter or the like may be further provided upstream of an
exhaust system, thereby trapping phosphorous utilizing a characteristic that phosphorous
tends to be absorbed in a place where a flow of exhaust gas is disturbed or in a first
member.
[0085] Further, although a diesel engine is described in this embodiment as an example of
an internal combustion engine to which the exhaust gas purifier in accordance with
the present invention is applied, it is needless to mention that the exhaust gas purifier
may be applied to a gasoline engine.
[0086] In the case of a gasoline engine, since a sulfur (S) component contained in fuel
is less but a phosphorous (P) component is contained in a greater amount compared
with those in the case of a diesel engine, calcium (Ca) and the phosphorous (P) component
tend to combine with each other to generate calcium phosphate (Ca
3(PO
4)
2) on a particulate filter.
[0087] According to the present invention, as described above, a metal having an electronegativity
equal to or lower than that of calcium (Ca) and strong ionization tendency (e.g.,
potassium (K)) is loaded on an ash trap provided upstream of the particulate filter,
whereby combining of potassium (K) or the like with the phosphorous (P) component
is given preference over the combining of calcium (Ca) with the phosphorous (P) component
and thus generation of (Ca
3(PO
4)
2) is inhibited. Therefore, the exhaust gas purifier in accordance with the present
invention is extremely effective for used in a gasoline engine.
[0088] In the exhaust gas purifier for an internal combustion engine in accordance with
the present invention is provided with an ash trap loaded with a basic metal upstream
of a collecting material, a component to be combined that forms ash when it combines
with a predetermined component is given preference in combining with the metal compared
with the predetermined component. Thus, formation of ash is inhibited.
[0089] Therefore, according to the present invention, in the exhaust gas purifier provided
with the collecting material for collecting particulate matters in exhaust gas, it
becomes possible to inhibit formation of ash, so that clogging of the collecting material
by ash is prevented and a function of the collecting material can be prevented from
being damaged.
[0090] Thus, it is seen that an exhaust gas purifier for an internal combustion engine is
provided. One skilled in the art will appreciate that the present invention can be
practiced by other than the preferred embodiments which are presented for the purposes
of illustration and not of limitation, and the present invention is limited only by
the claims which follow.