CN100419227C - Composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle - Google Patents
Composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle Download PDFInfo
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- CN100419227C CN100419227C CNB2005100476998A CN200510047699A CN100419227C CN 100419227 C CN100419227 C CN 100419227C CN B2005100476998 A CNB2005100476998 A CN B2005100476998A CN 200510047699 A CN200510047699 A CN 200510047699A CN 100419227 C CN100419227 C CN 100419227C
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Abstract
It relates to the particle filter and regeneration system of the diesel engine, made of carbide ceramics, comprising the power and particle filter. His particle filter and regeneration system of diesel engine comprises power, electric and nonelectric heat spiral particle filter made of carbide ceramics installing together inside the housing of the purifier connected with the exhaust of the diesel engine. It is highly efficient in purification and controllable in conductivity, and fine durability. Apart from that, it is low in cost, simple in structure and easy for assembly.
Description
Technical field
The present invention relates to a kind of diesel particulate filtration-regenerative system, specifically a kind of is the spiral composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle that combines with wall-flow type of employing of filtrating equipment carrier with the foam silicon carbide ceramics, can effectively reduce the particle emission of diesel-oil vehicle, and the regeneration of can switching on.
Background technique
Because the difference of mixing and burning mode, CO and HC lack much in the blowdown composition of diesel engine than petrol engine, and particulate is tens times of petrol engine even more.The complicated component of diesel particulate mainly is made up of soot and dissolved organic matter and part metals oxide.Soot mainly appears under the state of burning chamber of diesel engine high temperature anoxic and (quickens or big load as vehicle is anxious), at this moment, because of the diesel engine cycle fuel delivery increases severely, cause oil inflame bad, fuel oil splitting decomposition, polymerization, carbonization drain in the atmosphere with the form of dried soot (carbon by 85% and a spot of oxygen, hydrogen, sulphur, ash content and multiple polycyclic aromatic compound are formed); Dissolved organic matter mainly is made up of the fuel or the machine oil of not combustion, and the intermediate product of part for burning also arranged.The discharging of particulates in exhaust gas from diesel vehicle thing not only causes harmful effect to the healthy of people, and visually easier quilt intuitively discovers, thus the smoke evacuation of diesel-oil vehicle to purify be the emphasis that the diesel-oil vehicle blowdown is administered always.
The more diesel-oil vehicle smoke evacuation purification technics of research at present is particulate filter (DPF, a Diesel ParticulateFilter) technology.Particulate filter is followed micro particle filtering mechanism such as interception, inertial collision, diffusion, can reach high filtration efficiency by optimizing parameters such as aperture, surface area, packing density, volume.Yet along with accumulating of the particulate that filters, filtering hole will be stopped up gradually, and exhaust back pressure is increased, and cause engine power performance and Economy to worsen.Therefore must in time remove the particulate in the filter, just can make filter continue proper functioning.This process is called the regeneration of particulate filter.
The regenerated way of particulate filter has several, first kind is utilized catalyst regeneration, promptly add catalyzer on the particulate filter surface, utilize the catalysis of catalyzer to reduce the initiation temperature of particulate, make the particulate that captures at a lower temperature with tail gas in oxygen or nitrogen oxides reaction generate carbon dioxide and remove particulate.But this regenerated way requires the temperature of tail gas must reach certain requirement, and when travelling under automobile low speed or the heavy condition of underloading, exhaust temperature does not often reach this requirement; Second kind of regenerated way is to utilize the mode of heater or burning to improve the temperature of tail gas, particulate burnt under high temperature condition remove.Preceding two kinds of methods all are the in-situ regeneration modes, and filter still is positioned at former mounting point when promptly regenerating.The ex situ of being exactly regenerated way is arranged again, promptly work as particulate filter and be filled into after the particulate of some, particulate filter is heated from automobile removes equipment such as being put into air furnace, particle burning is removed.
Adopt which kind of regenerated way all to be faced with two problems: the one, the problem of regeneration efficiency, have again be exactly when regenerating particulate filter often because of the rapid heat release scorification of particle burning or burst.Must overcome during the novel particulate filter of this two problems design.
Summary of the invention
The object of the present invention is to provide a kind of composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle.This device is main raw material with the foam silicon carbide ceramics, adopts spiral and wall-flow type structure combining to carry out micro particle filtering, has realized the filtration respectively of different-diameter particulate.This device has the function of energising heating in-situ regeneration, with the power supply of Vehicular accumulator cell power supply as electric heating regeneration.
For achieving the above object, the technical solution used in the present invention is:
A kind of composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle, be grouped into by power supply, particulate filter and electric control part, particulate filter is divided into two-part, and a part is for having the spiral turbulent particulate filter (hereinafter abbreviating filter A as) of electric heating function; Another part is wall-flow type particulate filter (hereinafter abbreviating filter B as).Two metal films are connected on the silicon carbide ceramics electrode base at the spiral turbulent particulate filter of electric heating two ends in the mode of welding, and power supply constitutes the loop by metal film and the spiral turbulent particulate filter of electric heating, is its power supply.Filter A is with in filter B is installed on the purifier package casing that links to each other with diesel engine exhaust together, and automatically controlled part links to each other with the electrode of filter A.Spiral turbulent particulate filter of described electric heating and wall-flow type particulate filter adopt foam silicon carbide ceramics to make material.
Described filter A adopts sped structure, and its central position is one to have the spiral foam silicon carbide ceramics of a plurality of blades, parameter actual demand such as volume, gas flow changes per sample such as lobe numbers, spiral angle, pitch and the spiral degree of depth.At the foam silicon carbide ceramics of a tubulose of the peripheral suit of spiral foam silicon carbide ceramics, its internal diameter is consistent with the external diameter of spiral foam silicon carbide ceramics, guarantees that both can be in conjunction with closely.Exhaust gas from diesel vehicle is when flowing through filter, advance in spiral turbulent mode, particulate contained in the tail gas is when directly being filtered by spiral foam silicon carbide ceramics blade, and is most by in the centrifugal tubular silicon carbide foamed ceramics extremely all around, thereby reaches the purpose of micro particle filtering.
Can be catalyst-loaded on the described filter A, be carrier with the foam silicon carbide ceramics, the coating levels of every liter of carrier is at 80～130g, and the weight ratio of each material is in the coating: Al
2O
3: CeO
2: La
2O
3: BaO=50～75: 30～40: 2～8: 1～10; The used active substance of catalyzer can be Pt or Pd, and Pt or Pd total content are 1～5g in every liter of carrier.
Described filter B adopts the wall-flow type structure, form through bonding by multi-disc foam silicon carbide ceramics plate, tail gas enters the wall-flow type particulate filter by numerous delta-shaped regions, pass foam silicon carbide ceramics then and enter adjacency channel, import center hole by adjacency channel towards the slit of center hole more afterwards, discharge then outside the car, particulate obtains filtering in this course.The foamed ceramic panel of formation wall-flow type foamed ceramics particulate filter is combined by the foamed ceramic panel in two kinds (containing two kinds) above different apertures, and air inlet face is a large scale aperture plate, and the face of giving vent to anger is the minimum-value aperture plate.
Described filter B can adopt two foam silicon carbide ceramics plates to be one group and radially distribute, and the middle center hole that forms keeps 1.5mm～3mm gap between two foam silicon carbide ceramics plates, and open in center hole one side, other three limits are closed state; Abutting edge between group and the group keeps 1.5mm～3mm gap, and open at inlet end, other three limits are closed state; The center hole inlet end is sealed by silicon carbide ceramics, and tail gas flows into the wall-flow type particulate filter, passes the foam silicon carbide ceramics plate then and enters adjacent slit, flows out through center hole again.
Described foam silicon carbide ceramics is the mark meter by weight, and its composition is made up of 90%～98% silicon carbide and 10%～2% silicon.
Described foam silicon carbide ceramics is an elementary cell with polygonal closed loop, and each elementary cell is interconnected to form three-dimensional networks; Constitute relative density 〉=99% of the ceramic muscle of polygonal closed loop unit, average grain size is at 50nm～10 μ m.
The efficient of filter and the engine back pressure that causes can be by changing foam silicon carbide ceramics parameter adjustments such as ceramic volume fraction, mean pore size, filter volume.
The present invention adopts foam silicon carbide ceramics to make raw material, has designed and produced to have concurrently spiral and the particulate filters wall-flow type characteristics.The exhaust gas from diesel vehicle spiral turbulent particulate filter of at first flowing through, advance in spiral turbulent mode, major diameter particulate contained in the tail gas is when directly being filtered by spiral foam silicon carbide ceramics blade, the overwhelming majority by centrifugal to around the tubular silicon carbide foamed ceramics in, thereby reach the purpose of major diameter micro particle filtering.Then flow into the wall-flow type particulate filter from spiral turbulent particulate filter effluent air, at this, the particulate of minor diameter obtains filtering.In addition, be welded with two electrodes, utilize the electric conductivity of silicon carbide ceramics can be this filter heating in-situ regeneration of switching at spiral turbulent particulate filter two ends.Because foam silicon carbide ceramics has good thermal-shock resistance and high fusing point, the high temperature that produces during regeneration can not cause fusion or burst phenomenon in this filter.
Compared with prior art, the present invention has more following beneficial effect:
1. particulate filter is made of foam silicon carbide ceramics, and this filters has following characteristics: a, thermal conductivity good.Guarantee that filter temperature is evenly distributed, avoid the generation of excessive thermal stress and reduce the existence at regeneration dead angle; B, thermal-shock resistance are good, the jump in temperature that the particulate oxide burning causes in the time of can bearing regeneration; C, fusing point height, more than 2000 ℃, guaranteeing at high temperature has long working life.
2. realized in this device that electric heating heater and particulate filter are integrated, heating material is foam silicon carbide ceramics, and is simple in structure, and resistance can be adjusted according to actual needs flexibly.Silicon carbide ceramics has good anti-oxidant, high temperature resistance, anti acid alkali performance energy in addition, compares with metallic resistance silk heater, is more suitable for using in the vehicle exhaust environment.
3. filter adopts spiral composite structure in conjunction with wall-flow type, and can carry out specific aim according to the particulate of different sizes in the tail gas and filter, the filter efficiency height, back pressure is little.
5. this device adopts Vehicular accumulator cell as power supply, need not additional power source, and the automobile improvement scope is little, and cost is low;
6. control system intellectuality can be adjusted heated condition according to conditions such as water temperature, engine speed and back pressures in good time;
7. adopt the mode of soldering to prepare metal film, it is minimum that contact resistance is reduced to, and improved energy utilization efficiency;
8. apparatus of the present invention have good, controlled electric conductivity, after diesel particulate is effectively filtered, can realize intelligent regeneration, thereby have good endurance quality under the situation of vehicle power normal power supply.Simultaneously, it is low, simple in structure that apparatus of the present invention also have a cost, assembles characteristics such as easy.
Description of drawings
Fig. 1 is a composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle work schematic representation.
Fig. 2 is the sectional view of spiral turbulent particulate filter.
Fig. 3 is the profile of the spiral turbulent particulate filter of electric heating.
Fig. 4 is the sectional view of wall-flow type particulate filter.
Fig. 5 is the sectional drawing of wall-flow type particulate filter.
Fig. 6 is the structural representation of combined type foam silicon carbide ceramics plate.
Among the figure, 1 diesel engine; 2 cooling-water temperature sensors; 3 speed probes; 4 control units; 5 (PCC) powers; 6 Vehicular accumulator cells; 7 cables; 8 purifier package casings; 9 filter B; 10 metal films; 11 metal films; 12 filter A; 13 outlet pipes; 14 pressure transducers; 15 blades; 16 center potteries; 17 center holes; 18 tubular silicon carbide foamed ceramicses; 19 silicon carbide ceramics electrode bases; 20 silicon carbide ceramics electrode bases; 21 delta-shaped regions; 22 foam silicon carbide ceramics plates; 23 foam silicon carbide ceramics plates; 24 silicon carbide ceramics pieces; 25 blockade lines; 26 black lines; 27 center holes; 28 aperture foamed ceramic panels; 29 macropore foamed ceramic panels.
Embodiment
The preparation process of composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle is specific as follows:
1. adopt according to " foam silicon carbon stupalith of a kind of high strength dense and preparation method thereof " (Metal Inst., Chinese Academy of Sciences's application, application number 03134039.3, the applying date: on September 22nd, the 2003) conductive silicon carbide foam ceramic of being done, as spiral turbulent particulate filter of electric heating of the present invention and wall-flow type micro particle filtering modulator material.
2. silicon carbide foam ceramic material is processed into as Fig. 2～particulate filter shown in Figure 5.15 is the blade of spiral turbulent particulate filter, and its number can determine as the case may be.16 is the center pottery of spiral turbulent particulate filter, and 17 is the center hole of spiral turbulent particulate filter, and the two ends of center hole are silicon carbide ceramics electrode bases 19,20.18 for being enclosed in the tubular silicon carbide foamed ceramics around the spiral foam silicon carbide ceramics, and its effect mainly is to be captured in the particulate that enters under the centrifugal action.The parameters such as thickness of the lobe numbers of spiral turbulent particle capture device, length of blade and tubular silicon carbide foamed ceramics can change according to actual conditions; Being one group with 22,23 two such foam silicon carbide ceramics plates in the wall-flow type particulate filter radially distributes, middle formation between 27, two of the center holes keeps the 1.5mm gap, keeps open in center hole one side, other three limits are closed state, shown in the blockade line among Fig. 5 25.Group also keeps the 1.5mm gap with combination between the group on one side of being connected, open in the inlet end maintenance, and other three limits are closed state, shown in the black line among Fig. 5 26.The center hole inlet end forces the numerous delta-shaped regions 21 of tail gas from Fig. 4 to flow into the wall-flow type particulate filter by 24 sealings of a silicon carbide ceramics piece, passes the foam silicon carbide ceramics plate then and enters adjacent slit, imports center hole again and flows out.
3. at spiral turbulent particulate filter two ends silicon carbide ceramics electrode base 19,20 is arranged, two metal films 10,11 are connected on the silicon carbide ceramics electrode base 19,20 in the mode of welding, and just can obtain having the spiral turbulent particulate filter of electric heating regeneration function.
If 4. catalyst-loaded on filter A surface, be carrier with the foam silicon carbide ceramics, then supporting as follows of catalyzer carried out:
A, be to soak 5～10 minutes in the NaOH of 2～5M or the KOH solution in concentration, remove its surperficial impurity such as greasy dirt foam silicon carbide ceramics, afterwards water clean, oven dry in 1～4 hour in 100～150 ℃ of air atmospheres again;
B, get γ-Al
2O
3110～160 parts, CeO
250～70 parts, La
2O
34～0 parts of 2～10 parts, BaO add 500 parts in water after the mixing, ball milling obtained coating paste in 2～4 hours;
C, foam silicon carbide ceramics was flooded in slurry 2～5 minutes, blow away unnecessary slurry, placed 100～150 ℃ of air atmospheres then dry 20～30 minutes, flood slip after the cooling once more with pressurized air.So repeat repeatedly, until making coating levels reach 80～130g/ (L carrier), at last in 450～500 ℃ of roastings 4～5 hours, the coating preparation finishes;
D, get H
2PtCl
61-15 part adds water and is mixed with mixed solution for 500 parts, the foam silicon carbide ceramics that will have active coating then vacuum impregnation 10～15 minutes in solution, and the pottery behind the dipping is dried in baking oven, 100～150 ℃ of oven temperatures, 20～30 minutes time; Sample after the oven dry 450～500 ℃ of reductase 12～4 hour in hydrogen atmosphere, can to obtain with the foam silicon carbide ceramics be carrier, be the diesel vehicle soot filter with catalysis of catalytic active component with Pt.
5. filter A and filter B are packaged in the filter housing together, filter housing is welded by the corrosion resistant plate of 2 millimeters thick, between spiral turbulent particulate filter of filter housing and electric heating and the wall-flow type particulate filter shockproof interlayer is arranged.Filter after the encapsulation links to each other with diesel engine exhaust at inlet end.
Shown in Fig. 1～5, composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle comprises filter B 9, filter A 12 and automatically controlled part, and wherein filter B 9 is in filter A 12 is installed on the purifier package casing 8 that links to each other with diesel engine exhaust.Filter A 12 two ends are equipped with two metal films 11,10 that are welded on the silicon carbide ceramics electrode base 19,20, and power supply constitutes the loop by metal film 10,11 and filter A12, are filter A 12 power supplies; Automatically controlled part links to each other with the electrode 10,11 of filter A 12.Described automatically controlled part is made up of control unit 4 and (PCC) power 5.The automatically controlled part of the present invention adopts the Chinese invention patent application, application number: 200510046472.1, and the applying date: on May 20th, 2005, see wherein Fig. 5 and relevant explanatory note for details.
Figure 6 shows that combined type multilayer foam silicon carbide ceramics plate schematic representation, the foam silicon carbide ceramics plate that constitutes the wall-flow type particulate filter adopts composite structure, is combined by the foam silicon carbide ceramics plate in two or more different apertures and obtains having the filtration that changes the aperture.Tail gas is simultaneously flowed into by the large aperture foam plate, simultaneously flows out from the small aperture.Among the figure, aperture foamed ceramic panel 28 apertures are 0.01mm～0.5mm; Macropore foamed ceramic panel 29 apertures are 0.3mm～1.5mm.
Behind the automobile starting, the vehicle exhaust that contains the soot particulate is discharged by diesel engine 1, arrives filter A and filter B via outlet pipe 13, and filter A and filter B are with the particulate trap in the tail gas.The controlled unit 4 of cooling water water temperature, rotating speed and back pressure signal that is monitored by engine cooling water cooling-water temperature sensor 2 and speed probe 3 and pressure transducer 14 receives, and then transmits signals to (PCC) power 5.When back pressure is higher than setting value, all reach under the situation of specifying numerical value in cooling water water temperature and engine speed, (PCC) power 5 is connected circuit, and Vehicular accumulator cell 6 promptly begins to give filter A 12 power supplies by cable 7, and can be set current"on"time by control unit; 10 and 11 is two electrodes of filter A 12, and an end is soldered on the conductive silicon carbide foam ceramic, and the other end links to each other with cable; Under the energising situation, filter A 12 heats up rapidly, and the part soot that is filtered on it takes fire.The tail gas of heater of flowing through obtains the heat that heat that the spiral turbulent particulate filter conduction of electric heating comes and carbon-smoke combustion discharge, and temperature raises.The soot that tail gas after the intensification ignites and wherein filters through filter B the time also is purified filter B.
But exhaust gas cleaner of the present invention mainly is made of the spiral turbulent particulate filter of foam silicon carbide ceramics and intelligent control unit two-part of above-mentioned electric heating regeneration, filter is a function body with the foam silicon carbide ceramics, has good, controlled electric conductivity; And foam silicon carbide ceramics has the characteristics of porous, rough surface, high temperature resistant and thermal shock, cooperates spiral and wall-flow type structure can realize effective filtration to the emission of diesel engine particulate; But supported catalyst on filter; Intelligent control unit 4 can receive cooling water water temperature, back pressure and the engine rotational speed signal from the control unit platform, and according to the "on" position of signal from the main control composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle; Under the situation of vehicle power power supply, can realize the in-situ regeneration of system.
Embodiment and relevant comparative example
The engine model that adopts in the test of each embodiment and relevant comparative example is SOFIM8140.43, and test mode adopts diesel engine 13 operating modes.
1. the foam silicon carbide ceramics machining with volume fraction 30%, average foam aperture 1mm becomes the sped structure that six helical blades are arranged, and the spiral external diameter is φ 140mm, spiral degree of depth 50mm, vane thickness 10mm, blade pitgh 10mm, helical pitch 120mm, center hole φ 10mm.
2. the foam silicon carbide ceramics of machining tubulose, external diameter φ 180mm, internal diameter φ 140mm.
3. 2. the tubular silicon carbide foamed ceramics of gained is enclosed within the 1. sped structure periphery of gained, and both are used the silester strong bond, obtains spiral turbulent particulate filter.Boundary dimension is φ 180mm * 100mm.
4. get two silicon carbide ceramics electrode φ 20mm * 15mm, the two ends of the spiral turbulent particulate filter of φ 180mm * 100mm described in 3. the employing brazing mode is welded on are as the pedestal of metal film; The stainless steel column of a diameter 6mm of each soldering is as the electrode that links to each other with lead on the silicon carbide ceramics electrode base; Obtaining a profile is the spiral turbulent particulate filter with electric heating regeneration function of φ 180mm * 100mm.
5. as Fig. 4～Fig. 5, with the bonding circular wall-flow type structure of foam silicon carbide ceramics plate of thickness 4mm, volume fraction 30%, average foam aperture 0.5mm, final profile is φ 180mm * 250mm, and center hole is φ 40mm * 250mm.
6. the 4. middle spiral turbulent particulate filter of gained electric heating gained wall-flow type particulate filter in 5. is packaged in the purifier shell, obtains a complete electric heating regeneration combined type particulate filter.
7. 6. gained filtration-regenerative system is connected with motor, and the engine model that test is used is SOFIM8140.43, and test mode adopts diesel engine 13 operating modes; No electric circuit in the test process.
Difference from Example 1 is:
Before test, the spiral turbulent particulate filter of electric heating is installed on the specified position of diesel engine exhaust path, the maintenance engine speed is that 2160rpm, moment of torsion are that 188Nm, power are 42.5kW operation 5 hours, make the spiral turbulent particulate filter of electric heating fully gather soot, connect electric heating circuit then, carry out electric heating regeneration.Carry out 13 working condition measurements after the regeneration again with embodiment 1.
Difference from Example 1 is:
The foam silicon carbide ceramics volume fraction of forming spiral turbulent particulate filter of electric heating and wall-flow type particulate filter is 40%.
Embodiment 4
Difference from Example 2 is:
The foam silicon carbide ceramics volume fraction of forming spiral turbulent particulate filter of electric heating and wall-flow type particulate filter is 40%.
Difference from Example 1 is:
The foam silicon carbide ceramics volume fraction of forming spiral turbulent particulate filter of electric heating and wall-flow type particulate filter is 50%.
Difference from Example 2 is:
The foam silicon carbide ceramics volume fraction of forming spiral turbulent particulate filter of electric heating and wall-flow type particulate filter is 50%.
Difference from Example 1 is:
The foam silicon carbide ceramics volume fraction of forming spiral turbulent particulate filter of electric heating and wall-flow type particulate filter is 40%, and wherein the foam silicon carbide ceramics average pore size of the spiral turbulent particulate filter of electric heating is 0.5mm.
Difference from Example 2 is:
The foam silicon carbide ceramics volume fraction of forming spiral turbulent particulate filter of electric heating and wall-flow type particulate filter is 40%, and wherein the foam silicon carbide ceramics average pore size of the spiral turbulent particulate filter of electric heating is 0.5mm.
Embodiment 9
Difference from Example 1 is:
The foam silicon carbide ceramics volume fraction of forming the wall-flow type particulate filter is 40%, and ceramic plate is a composite structure, is specially the foam silicon carbide ceramics plate that 2mm is thick, average pore size is 0.5mm and adds the foam silicon carbide ceramics plate that 2mm is thick, average pore size is 0.03mm.
Difference from Example 2 is:
The foam silicon carbide ceramics volume fraction of forming the wall-flow type particulate filter is 40%, and ceramic plate is a composite structure, is specially the foam silicon carbide ceramics plate that 2mm is thick, average pore size is 0.5mm and adds the foam silicon carbide ceramics plate that 2mm is thick, average pore size is 0.03mm.
Difference from Example 3 is:
Filter surfaces has catalyst coatings, and coating levels is 80～130g/ (a L carrier), and the weight ratio of each material is in the coating: Al
2O
3: CeO
2: La
2O
3: BaO=55: 35: 3: 7.Pt content is 1.5g/ (L carrier).
Difference from Example 4 is:
Filter surfaces has catalyst coatings, and coating levels is 80～130g/ (a L carrier), and the weight ratio of each material is in the coating: Al
2O
3: CeO
2: La
2O
3: BaO=55: 35: 3: 7.Pt content is 1.5g/ (L carrier).
Relevant comparative example
At diesel engine 13 working condition measurements that carry out on the motor identical under the uneasy fixed filter condition with embodiment.
Embodiment and relevant comparative example the results are shown in Table 1.Test 1～12 in the table 1 and be embodiment, experiment 13 is relevant comparative example.Each embodiment is compared with the result of comparative example, can find under the situation that adopts the combined type foam silicon carbide ceramics, filter efficiency is up to more than 90%, filter efficiency is along with the increase of volume fraction and reducing of average pore size and increase, however the increase that reduces also can cause back pressure of the increase of volume fraction and average pore size.The adding of noble metal catalyst can significantly reduce the discharging of CO and THC, but is not very remarkable for the reduction effect of particle emission.Electric heating regeneration after-filter still can keep good filter efficiency, shows that composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle not only has good purification filtering performance, and can effective regeneration, has long working life.
Table 1
Claims (5)
1. composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle, it is characterized in that: comprise power supply, particulate filter, the composite structure that particulate filter adopts the spiral turbulent particulate filter of electric heating to combine with the wall-flow type particulate filter, wherein the spiral turbulent particulate filter of electric heating is in the wall-flow type particulate filter is installed on the purifier package casing that links to each other with diesel engine exhaust; Two metal films are connected on the silicon carbide ceramics electrode base at the spiral turbulent particulate filter of electric heating two ends in the mode of welding, and power supply constitutes the loop by metal film and the spiral turbulent particulate filter of electric heating, is its power supply; Spiral turbulent particulate filter of described electric heating and wall-flow type particulate filter adopt foam silicon carbide ceramics to make material; Described wall-flow type particulate filter is one group with two foam silicon carbide ceramics plates and radially distributes that the middle center hole that forms keeps 1.5mm～3mm gap between two foam silicon carbide ceramics plates, and open in center hole one side, other three limits are closed state; Abutting edge between group and the group keeps 1.5mm～3mm gap, and open at inlet end, other three limits are closed state; The center hole inlet end is sealed by silicon carbide ceramics, and tail gas flows into the wall-flow type particulate filter, passes the foam silicon carbide ceramics plate then and enters adjacent slit, flows out through center hole again.
2. according to the described composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle of claim 1, it is characterized in that: the central position of the spiral turbulent particulate filter of described electric heating is one to have the spiral foam silicon carbide ceramics of a plurality of blades, foam silicon carbide ceramics at a tubulose of the peripheral suit of spiral foam silicon carbide ceramics, its internal diameter is consistent with the external diameter of spiral foam silicon carbide ceramics, both combine closely, tail gas is advanced in spiral turbulent mode when flowing through filter.
3. according to the described composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle of claim 1, it is characterized in that: with the spiral turbulent particulate filter of electric heating is carrier, prepare the active oxidation aluminium paint thereon, and supported catalyst, the coating levels of every liter of carrier is 80～130g, and the weight ratio of each material is in the coating: Al
2O
3: CeO
2: La
2O
3: BaO=50～75: 30～40: 2～8: 1～10; The used active substance of catalyzer is Pt or Pd, and the Pt of every liter of carrier or Pd total content are 1～5g.
4. according to the described composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle of claim 1, it is characterized in that: the foamed ceramic panel of formation wall-flow type foamed ceramics particulate filter is combined by the foamed ceramic panel in two or more different apertures, air inlet face is a large scale aperture plate, and the face of giving vent to anger is the minimum-value aperture plate.
5. according to the described composite filtering-regeneration device for particulates in exhaust gas from diesel vehicle of claim 1, it is characterized in that: described foam silicon carbide ceramics is an elementary cell with polygonal closed loop, and each elementary cell is interconnected to form three-dimensional networks; Constitute relative density 〉=99% of the ceramic muscle of polygonal closed loop unit, average grain size is at 50nm～10 μ m; Described foam silicon carbide ceramics is the mark meter by weight, and its composition is made up of 90%～98% silicon carbide and 10%～2% silicon.
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| EP3805533A1 (en) * | 2019-01-24 | 2021-04-14 | Eberspächer Exhaust Technology GmbH | Exhaust gas heating element |
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| CN102031800B (en) * | 2010-11-24 | 2012-07-25 | 三一重机有限公司 | Hybrid power regeneration control method and device for excavator |
| CN103347611B (en) * | 2011-02-10 | 2016-01-20 | 丰田自动车株式会社 | Electrical heating type catalyst |
| ES2759498B2 (en) * | 2018-07-20 | 2021-07-26 | Univ Sevilla | FILTER FOR DIESEL ENGINE PARTICLES USING BIOMORPHIC SILICON CARBIDE |
| CN112221278A (en) * | 2020-09-23 | 2021-01-15 | 中国科学院金属研究所 | Power plant tail gas CO2Flue gas pre-purification system before trapping |
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| DE3017784A1 (en) * | 1980-05-09 | 1981-11-12 | Fichtel & Sachs Ag, 8720 Schweinfurt | Diesel engine exhaust afterburner - has soot filter and electric heating coil in contact with it |
| EP0742352A2 (en) * | 1995-05-12 | 1996-11-13 | Isuzu Ceramics Research Institute Co., Ltd. | Diesel particulate filter apparatus |
| EP0802309A1 (en) * | 1996-04-17 | 1997-10-22 | Hugo Eelbode | Device for the purification of combustion engine exhaust gas |
| DE19626908A1 (en) * | 1996-07-04 | 1998-01-08 | Gutmann Messtechnik Ag | Exhaust emissions cleaner for diesel engine vehicle |
| CN1600742A (en) * | 2003-09-22 | 2005-03-30 | 中国科学院金属研究所 | Compact foamy thyrite in high intensity and preparation method |
-
2005
- 2005-11-14 CN CNB2005100476998A patent/CN100419227C/en not_active Expired - Fee Related
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE3017784A1 (en) * | 1980-05-09 | 1981-11-12 | Fichtel & Sachs Ag, 8720 Schweinfurt | Diesel engine exhaust afterburner - has soot filter and electric heating coil in contact with it |
| EP0742352A2 (en) * | 1995-05-12 | 1996-11-13 | Isuzu Ceramics Research Institute Co., Ltd. | Diesel particulate filter apparatus |
| EP0802309A1 (en) * | 1996-04-17 | 1997-10-22 | Hugo Eelbode | Device for the purification of combustion engine exhaust gas |
| DE19626908A1 (en) * | 1996-07-04 | 1998-01-08 | Gutmann Messtechnik Ag | Exhaust emissions cleaner for diesel engine vehicle |
| CN1600742A (en) * | 2003-09-22 | 2005-03-30 | 中国科学院金属研究所 | Compact foamy thyrite in high intensity and preparation method |
Non-Patent Citations (2)
| Title |
|---|
| 汽车尾气净化新技术的研究. 杨振明.学位论文. 2002 * |
| 汽车尾气的电直热催化净化技术研究. 杜庆洋.学位论文. 2004 * |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP3805533A1 (en) * | 2019-01-24 | 2021-04-14 | Eberspächer Exhaust Technology GmbH | Exhaust gas heating element |
| US11698012B2 (en) | 2019-01-24 | 2023-07-11 | Purem GmbH | Exhaust gas heating element |
Also Published As
| Publication number | Publication date |
|---|---|
| CN1966943A (en) | 2007-05-23 |
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