JPH04300661A - Apparatus for treating fine particles in exhaust gas - Google Patents

Apparatus for treating fine particles in exhaust gas

Info

Publication number
JPH04300661A
JPH04300661A JP3064844A JP6484491A JPH04300661A JP H04300661 A JPH04300661 A JP H04300661A JP 3064844 A JP3064844 A JP 3064844A JP 6484491 A JP6484491 A JP 6484491A JP H04300661 A JPH04300661 A JP H04300661A
Authority
JP
Japan
Prior art keywords
exhaust
filter
conductive
wire mesh
particulates
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP3064844A
Other languages
Japanese (ja)
Inventor
Tetsuya Uehara
哲也 上原
Hideo Yoshikawa
吉川 英夫
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nissan Motor Co Ltd
Original Assignee
Nissan Motor Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nissan Motor Co Ltd filed Critical Nissan Motor Co Ltd
Priority to JP3064844A priority Critical patent/JPH04300661A/en
Publication of JPH04300661A publication Critical patent/JPH04300661A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To well ensure the collection of fine particles in exhaust gas without using high voltage. CONSTITUTION:A conductive adsorbing filter 3 collecting fine particles contained in combustion gas is provided to an exhaust gas passage through which combustion gas passes and a metal net 5 permitting the combustion gas containing fine particles to pass is provided to the exhaust gas passage 1 on the upstream side of the adsorbing filter 3. The metal net 5 is negatively charged by a DC power supply 7 and the adsorbing filter 3 is positively charged by said power supply 7 and the fine particles passing through the metal net 5 are negatively charged to be electrically attracted to the adsorbing filter 3 to be collected.

Description

【発明の詳細な説明】[Detailed description of the invention]

【0001】0001

【産業上の利用分野】この発明は、燃焼ガスに含まれる
排気微粒子を捕集して処理する排気微粒子処理装置に関
する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust particulate processing device that collects and processes exhaust particulates contained in combustion gas.

【0002】0002

【従来の技術】一般に、石油及び石炭などの化石燃料を
使用する内燃機関,ガスタービン,産業用ボイラ,発電
用ボイラ,湯沸かし器及び高温ガス炉などにおける燃焼
ガスや、アルコール燃料及びバイオマス燃料を燃焼させ
た場合の燃焼ガスの、排気中に含まれる煤や不純物(ダ
スト)などの排気微粒子をそのまま大気中に放出すると
、環境汚染を招き好ましくない。
[Prior Art] Generally, combustion gas, alcohol fuel, and biomass fuel are burned in internal combustion engines, gas turbines, industrial boilers, power generation boilers, water heaters, high-temperature gas furnaces, etc. that use fossil fuels such as oil and coal. If exhaust particulates such as soot and impurities (dust) contained in the combustion gas are released into the atmosphere as they are, it will cause environmental pollution, which is undesirable.

【0003】従来、大気中に放出する煤及び不純物など
の排気微粒子の量は、定置用の燃焼装置については厳し
く規制されている。その規制対策としては、電気集塵法
及びバグフィルタを用いる方法などがある。電気集塵法
は高電圧(6000〜10000V)を用いたコロナ放
電を利用して排気微粒子に電荷を与え、これを電界の作
用(クーロン力)により排気中から電気的に分離して捕
集するもので、静電的凝集作用によって排気微粒子の捕
集ができる。
Conventionally, the amount of exhaust particulates such as soot and impurities released into the atmosphere has been strictly regulated for stationary combustion devices. Countermeasures for this regulation include the electrostatic precipitator method and the use of bag filters. Electrostatic precipitation uses corona discharge with high voltage (6,000 to 10,000 V) to charge exhaust particulates, and then electrically separates them from the exhaust gas using the action of an electric field (Coulomb force) and collects them. It is possible to collect exhaust particulates through electrostatic coagulation.

【0004】一方、バグフィルタを利用したものは、排
気通路に設置したバグフィルタを排気が通過するときに
排気微粒子を捕集するものであるが、最近ではバグフィ
ルタの上流側に静電チャージを配置し、コロナ放電を利
用して排気中の煤やダストに電荷を与え、後段のバグフ
ィルタで吸着捕集する方法も採用されている。このとき
のコロナ放電には、4000V/cm程度の高電圧が印
加される。
On the other hand, those using bag filters collect exhaust particulates when the exhaust gas passes through the bag filter installed in the exhaust passage, but recently, electrostatic charges have been placed on the upstream side of the bag filter. Another method is to use corona discharge to charge the soot and dust in the exhaust gas, which is then adsorbed and collected by a bag filter in the subsequent stage. A high voltage of about 4000 V/cm is applied to the corona discharge at this time.

【0005】これら定置用に対し、移動用の自動車にお
けるディーゼル機関などでは、上記したような高電圧装
置とその電源を設置することは、取扱い上不便であり、
また経済的でないため、排気通路中にセラミックフィル
タを排気流れと直角になるよう設置し、このフィルタに
より排気微粒子を捕集するようにしたものがある。この
場合、排気中に含まれる排気微粒子がフィルタにおける
炭素繊維や微小炭素粒子の隙間を通過する際に、ここに
吸着または付着し、捕集した排気微粒子が所定量に達す
ると、電気ヒータなどで排気微粒子を燃焼させフィルタ
を再生する開発研究が行われている(特開昭63−65
113号公報参照)。
[0005] In contrast to these stationary engines, it is inconvenient to install the above-mentioned high-voltage device and its power source in diesel engines and the like in mobile cars.
Moreover, since it is not economical, there is a method in which a ceramic filter is installed in the exhaust passage so as to be perpendicular to the exhaust flow, and the filter collects exhaust particulates. In this case, when the exhaust particulates contained in the exhaust gas pass through the gaps between carbon fibers and minute carbon particles in the filter, they are adsorbed or attached thereto, and when the collected exhaust particulates reach a predetermined amount, they are heated by an electric heater, etc. Developmental research is being conducted to regenerate filters by burning exhaust particulates (Japanese Patent Laid-Open No. 1983-1965).
(See Publication No. 113).

【0006】[0006]

【発明が解決しようとする課題】しかしながら、上記定
置用における電気集塵法、及びバグフィルタ上流にコロ
ナ放電を発生させる方法では、高電圧を利用するので、
装置が大掛かりとなって取扱いが不便となる上、コスト
高を招き好ましくなく、またバグフィルタ自体は安定し
た集塵性能が得られるが、排気微粒子の堆積が進むこと
による圧力損失と、寿命及び交換作業などのメンテナン
スに問題がある。また、セラミックフィルタを用いたも
のでは、再生時に使用する電気ヒータなどに大電力を必
要とし、また排圧の上昇による燃費悪化が問題となるほ
か、排気微粒子が局所的に捕集されるなど捕集量が多く
なると、ヒータによる燃焼熱が過大となりフィルタ寿命
を低下させ、また逆に少ないと燃焼に至らず再生できな
くなる虞がある。
[Problems to be Solved by the Invention] However, in the above-mentioned stationary electrostatic precipitator method and the method of generating corona discharge upstream of the bag filter, high voltage is used.
The equipment is large-scale, inconvenient to handle, and undesirable as it increases costs.Furthermore, although the bag filter itself provides stable dust collection performance, it suffers from pressure loss due to the accumulation of exhaust particulates, and short service life and replacement. There is a problem with maintenance such as work. In addition, ceramic filters require a large amount of power for the electric heater used during regeneration, and there is also the problem of poor fuel efficiency due to increased exhaust pressure, and exhaust particles are locally trapped. If the amount collected is too large, the combustion heat generated by the heater will be excessive and the filter life will be shortened, and if the amount is too small, combustion may not occur and regeneration may not be possible.

【0007】そこでこの発明は、高電圧を用いることな
く、排気微粒子の捕集を良好に確保することを目的とし
ている。
[0007] Accordingly, an object of the present invention is to ensure good collection of exhaust particulates without using high voltage.

【0008】[0008]

【課題を解決するための手段】前記目的を達成するため
にこの発明は、燃焼ガスが通過する排気通路に、燃焼ガ
スに含まれる排気微粒子を捕集する導電性の捕集部材を
設け、この捕集部材の上流側の排気通路に、前記排気微
粒子を含む燃焼ガスが排気微粒子とともに通過可能な導
電性部材を設け、この導電性部材と前記捕集部材とに互
いに極性の異なる電荷を帯電させる電圧印加手段を設け
たものである。
[Means for Solving the Problems] In order to achieve the above object, the present invention provides an electrically conductive collection member for collecting exhaust particulates contained in the combustion gas in the exhaust passage through which the combustion gas passes. A conductive member through which the combustion gas containing the exhaust particulates can pass together with the exhaust particulates is provided in the exhaust passage on the upstream side of the collection member, and the conductive member and the collection member are charged with charges having mutually different polarities. A voltage applying means is provided.

【0009】[0009]

【作用】電圧印加手段により、例えば導電性部材に負の
電荷を与える一方、捕集部材に正の電荷を与えると、排
気微粒子は排気とともに導電性部材を通過する際に負の
電荷を帯び、この負の電荷を帯びた排気微粒子が後段の
正の電荷を帯びた捕集部材に達すると、排気微粒子は捕
集部材に吸着され捕集される。
[Operation] When a voltage applying means applies a negative charge to the conductive member and a positive charge to the collection member, for example, the exhaust particulates become negatively charged when passing through the conductive member together with the exhaust gas. When the negatively charged exhaust particles reach the positively charged collecting member at the subsequent stage, the exhaust particles are attracted and collected by the collecting member.

【0010】0010

【実施例】以下、この発明の実施例を図面に基づき説明
する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Examples of the present invention will be described below with reference to the drawings.

【0011】図1及び図2はこの発明の原理を示す説明
図である。燃焼ガスが通過する排気通路1には、排気中
の煤やダストなどの排気微粒子を捕集する捕集部材であ
る炭素繊維フェルトなどの導電性吸着フィルタ3が設け
られている。導電性吸着フィルタ3は、石炭及び石油の
ピッチ系、ポリアクリルニトリル(PAN)系及びフェ
ノール系の炭素繊維、並びに金属及び非鉄性金属繊維を
用い、またその形状は、原綿、フェルト、マット、クロ
ス、ヤーン、シート及びチョップ状などでよい。ピッチ
系炭素繊維は、等方性ピッチや光学的異方性のメソフェ
ーズピッチなどを原料としている。炭化焼成処理は通常
600〜1500℃程度であるため耐熱性があるが、特
に800〜1000℃程度が望ましく、この場合直毛ま
たはカル状のピッチ系炭素繊維を用いる。炭素繊維の比
重は約2.5、線径は1〜15μm、嵩密度が20〜1
20kg/m3 程度がよい。
FIGS. 1 and 2 are explanatory diagrams showing the principle of the present invention. An exhaust passage 1 through which combustion gas passes is provided with a conductive adsorption filter 3 made of carbon fiber felt or the like, which is a collection member that collects exhaust particulates such as soot and dust in the exhaust gas. The conductive adsorption filter 3 uses coal and petroleum pitch-based, polyacrylonitrile (PAN)-based and phenol-based carbon fibers, as well as metal and non-ferrous metal fibers, and its shapes include raw cotton, felt, mat, and cloth. , yarn, sheet, chopped form, etc. Pitch-based carbon fibers are made from isotropic pitch, optically anisotropic mesophase pitch, and the like. The carbonization firing process is usually about 600 to 1500°C, so it is heat resistant, but it is particularly preferably about 800 to 1000°C, and in this case, straight or curly pitch-based carbon fibers are used. The specific gravity of carbon fiber is approximately 2.5, the wire diameter is 1 to 15 μm, and the bulk density is 20 to 1.
Approximately 20 kg/m3 is good.

【0012】このような導電性吸着フィルタ3の上流側
の排気通路1には、図2に示すように前記排気微粒子を
含むを燃焼ガスが排気微粒子とともに通過可能な導電性
部材としての金網5が設けられている。この金網5と前
記導電性吸着フィルタ3とは、これら相互に極性の異な
る電荷を帯電させる電圧印加手段としての、12Vある
いは24Vの直流電源7が接続されている。
As shown in FIG. 2, the exhaust passage 1 on the upstream side of the conductive adsorption filter 3 is provided with a wire mesh 5 as a conductive member through which the combustion gas containing the exhaust particles can pass together with the exhaust particles. It is provided. The wire mesh 5 and the conductive adsorption filter 3 are connected to a 12V or 24V DC power source 7, which serves as voltage application means for charging them with charges of mutually different polarities.

【0013】導電性吸着フィルタ3と金網5との間にお
ける排気通路1の下部には、排気微粒子を受け入れる煤
トレイ9が設置され、煤トレイ9における導電性吸着フ
ィルタ3の近傍には排気微粒子を燃焼させる電熱ヒータ
11が設けられている。この電熱ヒータ11は煤トレイ
9に落した煤自体を燃焼させるだけであるので、供給さ
れる電力は小さくてよい。
A soot tray 9 for receiving exhaust particulates is installed at the lower part of the exhaust passage 1 between the conductive adsorption filter 3 and the wire mesh 5, and a soot tray 9 near the conductive adsorption filter 3 is installed to receive the exhaust particulates. An electric heater 11 for combustion is provided. Since this electric heater 11 only burns the soot itself dropped into the soot tray 9, the supplied electric power may be small.

【0014】このような構成の排気微粒子処理装置にお
いて、直流電源7により導電性吸着フィルタ3に正の電
荷を与え、金網5に負の電荷を与える。この状態で、こ
の装置上流側で燃焼ガスが発生し、図中で矢印Aのよう
にその排気が流れてくると、排気は負に帯電した金網5
を通過しこれに接触することで、電気的に中性な煤やダ
ストなどの排気微粒子は負に帯電する。負に帯電した排
気微粒子が正に帯電している導電性吸着フィルタ3に達
すると、排気微粒子はこのフィルタ3の表面に電気的に
吸着して捕集され、その後付着表面で電気的に中性に戻
る。
In the exhaust particulate processing apparatus having such a configuration, the DC power supply 7 applies a positive charge to the conductive adsorption filter 3 and applies a negative charge to the wire mesh 5. In this state, when combustion gas is generated on the upstream side of this device and the exhaust gas flows as shown by arrow A in the figure, the exhaust gas flows through the negatively charged wire mesh 5.
By passing through and coming into contact with this, electrically neutral exhaust particles such as soot and dust become negatively charged. When the negatively charged exhaust particles reach the positively charged conductive adsorption filter 3, the exhaust particles are electrically adsorbed and collected on the surface of the filter 3, and then become electrically neutral on the adhering surface. Return to

【0015】このようにして排気微粒子の捕集量が増大
し、導電性吸着フィルタ3を再生する必要が生じると、
前記とは逆に導電性吸着フィルタ3に負の電荷を与え、
金網5に正の電荷を与える。これにより、導電性吸着フ
ィルタ3に付着している中性の排気微粒子は、負の電荷
を帯び、正電荷を帯びた金網5に吸い寄せられて移動し
、導電性吸着フィルタ3近傍の煤トレイ9に落下する。 煤トレイ9に落下した排気微粒子は、電熱ヒータ11に
より焼却される。導電性吸着フィルタ3に付着している
煤を煤トレイ9に落下させるためには、導電性吸着フィ
ルタ3と金網5との間隔を、電源7の電圧に応じて適宜
設定すればよい。
[0015] When the amount of collected exhaust particulates increases in this way and it becomes necessary to regenerate the conductive adsorption filter 3,
Contrary to the above, applying a negative charge to the conductive adsorption filter 3,
Give a positive charge to the wire mesh 5. As a result, the neutral exhaust particulates adhering to the conductive adsorption filter 3 are negatively charged, are attracted to the positively charged wire mesh 5, and are moved to the soot tray 9 near the conductive adsorption filter 3. to fall. The exhaust particles that have fallen onto the soot tray 9 are incinerated by the electric heater 11. In order to cause the soot adhering to the conductive suction filter 3 to fall onto the soot tray 9, the distance between the conductive suction filter 3 and the wire mesh 5 may be appropriately set according to the voltage of the power source 7.

【0016】上記のような排気微粒子処理装置によれば
、市販常用の100V、あるいは自動車用の12〜24
Vの低電圧電源を用い、高電圧を利用する必要がないの
で、装置が簡略化され、取扱い上も有利となってコスト
低下が達成される。また、排気微粒子は導電性吸着フィ
ルタ3の表面、あるいは表面付近に電気的に吸着し始め
るので、この状態で再生するようにすれば、排気微粒子
は導電性吸着フィルタ3の内部に入り込みにくくなり、
排気微粒子の堆積による排気圧力の上昇を防止でき、燃
料消費量の増加などによる機関性能の低下は防止される
。このように、排気微粒子は導電性吸着フィルタ3の内
部に入り込みにくいことからここを通過しにくくなり、
このため導電性吸着フィルタ3自体の目を荒くしたり、
排気流れ方向の厚さを薄くすることができ、これによっ
ても排気圧力の上昇を防止できる。また、導電性吸着フ
ィルタ3を再生させる際には、このフィルタ3に吸着し
た状態の排気微粒子を燃焼させるのではなく、逆極性の
電圧を導電性吸着フィルタ3と金網5との間に印加させ
て離脱させ落下させるので、導電性吸着フィルタ3の寿
命低下は回避され、フィルタ3の再生も良好に行われる
According to the above-described exhaust particulate treatment device, the commercially available 100V or the 12 to 24V for automobiles can be used.
Since a low voltage power supply of V is used and there is no need to use a high voltage, the device is simplified and is advantageous in terms of handling, resulting in cost reduction. Furthermore, since the exhaust particulates begin to be electrically adsorbed on or near the surface of the conductive adsorption filter 3, if regeneration is performed in this state, the exhaust particulates will be less likely to enter the inside of the conductive adsorption filter 3.
It is possible to prevent an increase in exhaust pressure due to the accumulation of exhaust particulates, and to prevent a decrease in engine performance due to an increase in fuel consumption. In this way, it is difficult for exhaust particulates to enter the inside of the conductive adsorption filter 3, making it difficult for them to pass through there.
For this reason, the mesh of the conductive adsorption filter 3 itself may be made rough, or
The thickness in the exhaust flow direction can be made thinner, which also prevents the exhaust pressure from increasing. Furthermore, when regenerating the conductive adsorption filter 3, instead of burning the exhaust particulates adsorbed on the filter 3, a voltage of opposite polarity is applied between the conductive adsorption filter 3 and the wire mesh 5. Since the conductive adsorption filter 3 is detached and dropped, a decrease in the life of the conductive adsorption filter 3 is avoided, and the filter 3 is regenerated well.

【0017】次に、この発明を自動車用ディーゼル機関
に適用した例を図3に示す。機関本体13に接続される
排気マニホールド15に排気管17が接続され、この排
気管17の途中に排気微粒子処理装置19が設けられて
いる。排気微粒子処理装置19はフィルタ箱21を有し
、このフィルタ箱21には、フィルタ箱21の内部空間
を上流側空間23と下流側空間25とに分割する捕集部
材としての炭素繊維フェルトからなる導電性のフィルタ
27が収納されている。フィルタ27とフィルタ箱21
との間には、耐熱性が高く電気的に高抵抗の例えばセラ
ミックなどからなる絶縁物29が介装されている。フィ
ルタ箱21の排気流に直交する面の断面積は、排気管1
7の同断面積より大きく形成し、排気管17からフィル
タ箱21に流出する排気の流速を低下させている。
Next, an example in which the present invention is applied to an automobile diesel engine is shown in FIG. An exhaust pipe 17 is connected to an exhaust manifold 15 connected to the engine body 13, and an exhaust particulate processing device 19 is provided in the middle of the exhaust pipe 17. The exhaust particulate processing device 19 has a filter box 21, which is made of carbon fiber felt as a collection member that divides the internal space of the filter box 21 into an upstream space 23 and a downstream space 25. A conductive filter 27 is housed. Filter 27 and filter box 21
An insulator 29 made of, for example, ceramic and having high heat resistance and high electrical resistance is interposed between the two. The cross-sectional area of the filter box 21 perpendicular to the exhaust flow is the same as that of the exhaust pipe 1.
7 in the same cross-sectional area to reduce the flow velocity of exhaust gas flowing out from the exhaust pipe 17 to the filter box 21.

【0018】上流側空間23には上流側排気管17aの
端部が挿入されて接続され、下流側空間25には下流側
排気管17bが連通接続されている。上流側空間23内
に位置する上流側排気管17a内には、導電性部材とし
ての金網31が設けられている。この金網31と上流側
排気管17aとの間には、セラミックなどからなる絶縁
物33が介装されている。金網31と前記フィルタ27
とは、12Vあるいは24Vの直流電源35が接続され
てる。フィルタ27と金網31との間におけるフィルタ
箱21の下部には煤トレイ37が設置され、煤トレイ3
7のフィルタ27の近傍には排気微粒子を燃焼させる電
熱ヒータ39が設けられている。
An end of an upstream exhaust pipe 17a is inserted into and connected to the upstream space 23, and a downstream exhaust pipe 17b is connected to the downstream space 25 in communication. A wire mesh 31 as a conductive member is provided in the upstream exhaust pipe 17a located in the upstream space 23. An insulator 33 made of ceramic or the like is interposed between the wire mesh 31 and the upstream exhaust pipe 17a. Wire mesh 31 and the filter 27
is connected to a 12V or 24V DC power supply 35. A soot tray 37 is installed at the bottom of the filter box 21 between the filter 27 and the wire mesh 31.
An electric heater 39 is provided near the filter 27 of No. 7 to burn exhaust particulates.

【0019】金網31が設けられた部位付近の詳細を図
4に示す。金網31は絶縁物33の上下流両端部付近の
内面にそれぞれ設けられ、2つの金網31,31相互間
には金網31,31に接触した状態で導電性の一対のス
ペーサ41が介装され、スペーサ41に電源35の負極
側が接続されている。
FIG. 4 shows details of the vicinity of the area where the wire mesh 31 is provided. The wire mesh 31 is provided on the inner surface near both the upstream and downstream ends of the insulator 33, and a pair of conductive spacers 41 are interposed between the two wire meshes 31, 31 in contact with the wire meshes 31, 31. The negative electrode side of the power source 35 is connected to the spacer 41 .

【0020】このように構成することで、フィルタ27
に正の電荷を与える一方、金網31に負の電荷を与え、
この状態で排気中の電気的に中性の排気微粒子は、金網
31を通過するときこれに接触して負の電荷を帯びる。 ここでは、金網31は直列に2つ配置されているので、
上流側の金網31で負に帯電できなかった排気微粒子も
下流側の金網31で負に帯電させることが可能となる。 排気は、この負に帯電した排気微粒子とともに上流側空
間23に流出し、ここで膨脹して流速が低下し、この状
態で排気微粒子はフィルタ27の表面に電気的に効率よ
く吸着し、吸着後中性に戻る。その後、フィルタ27及
び金網31に、それぞれ前記とは逆極性の電荷を帯電さ
せることで、排気微粒子を煤トレイ37上に落下させ燃
焼させる。  図5は、フィルタ箱21内の導電性のフ
ィルタ27直前に、金網43を絶縁物45を介して装着
したものである。この場合、金網43を上流側排気管1
7a内に設置せず、フィルタ27とともにフィルタ箱2
1内に設けてあるので、排気微粒子処理装置を一つのユ
ニットとして作成でき、取扱い上有利となる。
With this configuration, the filter 27
while giving a positive charge to the wire mesh 31, giving a negative charge to the wire mesh 31,
In this state, when the electrically neutral exhaust particles in the exhaust gas pass through the wire mesh 31, they come into contact with the wire mesh 31 and are negatively charged. Here, two wire meshes 31 are arranged in series, so
Exhaust particles that could not be negatively charged by the upstream wire mesh 31 can also be negatively charged by the downstream wire mesh 31. The exhaust gas flows into the upstream space 23 together with the negatively charged exhaust particles, where they expand and the flow velocity decreases. In this state, the exhaust particles are electrically and efficiently adsorbed to the surface of the filter 27, and after adsorption, Return to neutral. Thereafter, the filter 27 and the wire mesh 31 are each charged with charges of opposite polarity to those described above, so that the exhaust particulates fall onto the soot tray 37 and are burned. In FIG. 5, a wire mesh 43 is attached to the filter box 21 immediately in front of the conductive filter 27 with an insulator 45 interposed therebetween. In this case, the wire mesh 43 is connected to the upstream exhaust pipe 1
7a, and the filter box 2 together with the filter 27.
1, the exhaust particulate treatment device can be made as a single unit, which is advantageous in terms of handling.

【0021】図6は、フィルタ箱47内の下流側部位に
、導電性のフィルタ49を絶縁物50を介して設けてい
る。このフィルタ49は、下流側端面49a及び円筒部
49bからなるカップ状を呈し、絶縁物50もフィルタ
49と同形状を呈している。上流側排気管51は、その
下流側端部がフィルタ箱47内におけるフィルタ49内
の空間53に臨んでおり、下流側排気管55の上流側端
部もこの空間53に臨んでいる。フィルタ箱47内にお
ける上流側排気管51の空間53より上流側部分には、
導電性部材としての金網57が介装されている。金網5
7は、セラミックからなる一対の絶縁物59,59を介
してフランジ61,61間に挟持固定され、フィルタ箱
47内にも外周部が露出している。下流側排気管55と
フィルタ49との間には、セラミック製の絶縁物63が
介装されている。
In FIG. 6, a conductive filter 49 is provided at the downstream side of a filter box 47 with an insulator 50 interposed therebetween. This filter 49 has a cup shape consisting of a downstream end surface 49a and a cylindrical portion 49b, and the insulator 50 also has the same shape as the filter 49. The downstream end of the upstream exhaust pipe 51 faces a space 53 within the filter 49 in the filter box 47, and the upstream end of the downstream exhaust pipe 55 also faces this space 53. In the portion upstream of the space 53 of the upstream exhaust pipe 51 in the filter box 47,
A wire mesh 57 is interposed as a conductive member. wire mesh 5
7 is clamped and fixed between flanges 61 and 61 via a pair of insulators 59 and 59 made of ceramic, and its outer peripheral portion is also exposed inside the filter box 47 . A ceramic insulator 63 is interposed between the downstream exhaust pipe 55 and the filter 49.

【0022】このような構成によれば、直流電源35に
よりフィルタ49を正の電荷に、金網57を負の電荷に
それぞれ帯電させる。この状態で、上流側排気管51に
排気が流れてくると、排気は負に帯電した金網57を通
過しこれに接触することで、電気的に中性な煤やダスト
などの排気微粒子は負に帯電する。負に帯電した排気微
粒子がフィルタ49内の空間53に達すると、正に帯電
しているフィルタ49に電気的に吸着し、付着表面で電
気的に中性に戻る。
According to this configuration, the DC power supply 35 charges the filter 49 with a positive charge and the wire mesh 57 with a negative charge. In this state, when exhaust gas flows into the upstream exhaust pipe 51, the exhaust gas passes through and comes into contact with the negatively charged wire mesh 57, so that electrically neutral exhaust particles such as soot and dust are removed from the negatively charged wire mesh 57. is charged with electricity. When the negatively charged exhaust particles reach the space 53 within the filter 49, they are electrically adsorbed to the positively charged filter 49 and return to electrical neutrality on the adhering surface.

【0023】排気微粒子の捕集量が増大しフィルタ49
を再生する必要が生じると、前記とは逆にフィルタ49
を負の電荷に帯電させ、金網57を正の電荷に帯電させ
る。これにより、フィルタ49に付着している中性の排
気微粒子は、負の電荷を帯び、正電荷を帯びた金網57
の外周部に吸い寄せられて移動し、煤トレイ37に落下
する。煤トレイ37に落下した排気微粒子は、電熱ヒー
タ39により焼却される。
[0023] The amount of collected exhaust particulates increases, and the filter 49
When it becomes necessary to regenerate the filter 49, contrary to the above
is charged with a negative charge, and the wire mesh 57 is charged with a positive charge. As a result, the neutral exhaust particles adhering to the filter 49 are negatively charged, and the wire mesh 57 is positively charged.
The soot is attracted to the outer periphery of the soot and moves, and falls into the soot tray 37. The exhaust particles that have fallen onto the soot tray 37 are incinerated by the electric heater 39.

【0024】この場合には、排気は排気上流管51から
フィルタ箱47内に一旦流出した後排気下流管55に流
入し、フィルタ49を通過することがないので、圧力損
失を低く抑えることができ、排気圧力も排気がフィルタ
49を通過するものに比べて小さく、燃料消費量も少な
くて済み機関出力も向上する。また、上流側排気管51
を流れる排気が一旦フィルタ箱47内に流出して拡張す
るので、排気消音効果も得られる。
In this case, the exhaust gas flows from the exhaust upstream pipe 51 into the filter box 47 and then flows into the exhaust downstream pipe 55 without passing through the filter 49, so that pressure loss can be kept low. The exhaust pressure is also lower than that when exhaust gas passes through the filter 49, resulting in less fuel consumption and improved engine output. In addition, the upstream exhaust pipe 51
Since the exhaust gas flowing through the filter box 47 once flows out and expands, an exhaust silencing effect can also be obtained.

【0025】図7は、フィルタ箱63内に、導電性のフ
ィルタ65をその嵩密度を考慮して排気流れに直角に配
置したもので、これによりフィルタ箱63内は上流側空
間67と下流側空間69とに分割される。符号64は絶
縁物である。そして、上流側空間67に図6と同様な上
流側排気管51を、また下流側空間69には下流側排気
管55をそれぞれ臨ませている。この例では、図6と同
様に排気消音効果が得られるほか、排気がフィルタ65
を通過するので、図6のものに比べ排気圧力は高まるが
、排気微粒子の除去効果は向上する。
FIG. 7 shows a filter box 63 in which a conductive filter 65 is arranged perpendicularly to the exhaust flow in consideration of its bulk density, so that the interior of the filter box 63 is divided into an upstream space 67 and a downstream space. It is divided into a space 69. Reference numeral 64 is an insulator. An upstream exhaust pipe 51 similar to that shown in FIG. 6 faces the upstream space 67, and a downstream exhaust pipe 55 faces the downstream space 69. In this example, in addition to obtaining the exhaust silencing effect as in FIG.
6, the exhaust pressure is higher than that in FIG. 6, but the effect of removing exhaust particulates is improved.

【0026】図8は、フィルタ箱71内の金網43の下
流に設置する導電性のフィルタ73を排気流れと平行に
複数設けたものである。フィルタ73を排気流れと平行
に設けることで、図6の例と同様に排気圧力を低くを抑
えることができる。
FIG. 8 shows a filter box 71 in which a plurality of conductive filters 73 are installed downstream of the wire mesh 43 in parallel to the exhaust flow. By providing the filter 73 in parallel with the exhaust flow, the exhaust pressure can be kept low as in the example of FIG.

【0027】次に、500cc単気筒4サイクルディー
ゼル機関(直接噴射式)にこの発明を適用した場合の試
験結果を図9に示す。図9は、フィルタ箱の入口と出口
とにおける排気中の煤濃度の変化率(%)と、機関出力
(PS)との関係を、機関回転数が2600rpmの状
態で印加電圧の違いにより示したものである。ここで、
実線が0V,破線が12V,一点鎖線が24V,二点鎖
線が50Vをそれぞれ印加したとき濃度変化率である。 また、フィルタ箱の形式は、図6のものを使用した。こ
れによれば、12V,24V,50Vと各電圧を印加し
た場合には、電圧を印加せず、単にフィルタを設置した
場合に比べてフィルタ箱入口に対する同出口の濃度変化
が大きく、煤がより多く除去されていることがわかる。
Next, FIG. 9 shows test results when the present invention was applied to a 500cc single-cylinder four-stroke diesel engine (direct injection type). Figure 9 shows the relationship between the rate of change (%) of the soot concentration in the exhaust gas at the inlet and outlet of the filter box and the engine output (PS) at an engine speed of 2,600 rpm with different applied voltages. It is something. here,
The solid line shows the concentration change rate when 0V is applied, the broken line shows 12V, the one-dot chain line shows 24V, and the two-dot chain line shows the concentration change rate when 50V is applied. Furthermore, the filter box format shown in FIG. 6 was used. According to this, when voltages of 12V, 24V, and 50V are applied, the concentration change at the filter box outlet relative to the filter box entrance is larger than when no voltage is applied and a filter is simply installed, and the soot is more It can be seen that much has been removed.

【0028】図10は、機関始動時におけるフィルタ箱
出口での煤濃度(%)と、印加電圧(V)との関係を示
している。これによれば、単にフィルタを設置した場合
の煤濃度が89%に対し、電圧を12V印加した場合に
は72%と大きく低下し、さらに印加電圧を24V,5
0Vと大きくするに従い、煤濃度は68%,65%と徐
々に低下している。なお、このときのフィルタ箱入口の
煤濃度は96%である。  これらの試験結果からも明
らかなように、排気微粒子に負の電荷を与えてこれを正
の電荷を帯びているフィルタに吸着させることで、効果
的に排気微粒子を除去することができる。
FIG. 10 shows the relationship between the soot concentration (%) at the outlet of the filter box and the applied voltage (V) when the engine is started. According to this, the soot concentration was 89% when a filter was simply installed, but it significantly decreased to 72% when a voltage of 12V was applied.
As the voltage increases to 0V, the soot concentration gradually decreases to 68% and 65%. Note that the soot concentration at the entrance of the filter box at this time was 96%. As is clear from these test results, exhaust particulates can be effectively removed by giving them a negative charge and causing them to be adsorbed by a positively charged filter.

【0029】なお、上記実施例では、排気微粒子に金網
を通過せる際に負の電荷を与えているが、これとは逆に
このとき排気微粒子に正の電荷を与えるよう金網に正の
電荷を、フィルタに負の電荷を与えるようにし、排気微
粒子がフィルタに付着した後に、金網に負の電荷を、フ
ィルタに正の電荷を与える構成としてもよい。また、具
体例としてディーゼル機関を用いて説明したが、これに
限ることはなく、石油及び石炭などの化石燃料を使用す
るガスタービン,産業用ボイラ,発電用ボイラ,湯沸か
し器及び高温ガス炉や、アルコール燃料及びバイオマス
燃料を燃焼させるシステムに、この発明を適用してもよ
い。
In the above embodiment, a negative charge is given to the exhaust particulates when they pass through the wire mesh, but on the contrary, a positive charge is given to the wire mesh so that the exhaust particulates are given a positive charge at this time. , a negative charge may be applied to the filter, and after the exhaust particles adhere to the filter, a negative charge may be applied to the wire mesh and a positive charge may be applied to the filter. Although the explanation is given using a diesel engine as a specific example, the explanation is not limited to this, but includes gas turbines that use fossil fuels such as oil and coal, industrial boilers, power generation boilers, water heaters, high-temperature gas furnaces, alcohol The present invention may be applied to systems that burn fuel and biomass fuel.

【0030】[0030]

【発明の効果】以上説明してきたようにこの発明によれ
ば、排気通路に設けた排気微粒子を捕集する導電性の捕
集部材の上流側に、燃焼ガスが通過可能な導電性部材を
設け、これら捕集部材及び導電性部材間に電圧を印加し
、電荷を帯びた導電性部材を通過する排気微粒子を帯電
させ、その下流の捕集部材に電気的に吸着させて捕集す
るようにしたので、使用電圧は低電圧のもので済み、装
置が簡略化でき、取扱い上も有利となってコスト低下を
達成することができる。また、捕集部材に吸着する排気
微粒子は、捕集部材の表面から付着し始めるので、捕集
部材の内部には入りにくく、この状態で捕集部材及び導
電性部材間に上記とは逆極性の電荷を帯電させることで
排気微粒子を落下させれば、排気圧力の上昇が最小限に
抑えられ、捕集部材の再生をその寿命を低下させること
なく良好に行うことができる。
As explained above, according to the present invention, a conductive member through which combustion gas can pass is provided upstream of a conductive collection member provided in the exhaust passage for collecting exhaust particulates. , a voltage is applied between the collection member and the conductive member to charge the exhaust particles passing through the charged conductive member, so that they are electrically attracted to the downstream collection member and collected. Therefore, only a low voltage can be used, and the device can be simplified, which is advantageous in terms of handling, and cost reduction can be achieved. In addition, since the exhaust particulates adsorbed to the collection member start adhering from the surface of the collection member, it is difficult for them to enter the inside of the collection member, and in this state, the polarity opposite to the above is formed between the collection member and the conductive member. If the exhaust particulates are caused to fall by being charged with an electric charge, the increase in exhaust pressure can be minimized, and the collection member can be regenerated well without reducing its life.

【図面の簡単な説明】[Brief explanation of drawings]

【図1】この発明の排気微粒子処理装置の原理を示す説
明図である。
FIG. 1 is an explanatory diagram showing the principle of an exhaust particulate treatment device of the present invention.

【図2】図1のB−B断面図である。FIG. 2 is a sectional view taken along line BB in FIG. 1;

【図3】この発明の第1の実施例を示す全体構成図であ
る。
FIG. 3 is an overall configuration diagram showing a first embodiment of the present invention.

【図4】図3の金網部分の拡大された断面図である。FIG. 4 is an enlarged cross-sectional view of the wire mesh portion of FIG. 3;

【図5】この発明の第2の実施例を示す排気微粒子処理
装置の断面図である。
FIG. 5 is a sectional view of an exhaust particulate treatment device showing a second embodiment of the present invention.

【図6】この発明の第3の実施例を示す排気微粒子処理
装置の断面図である。
FIG. 6 is a cross-sectional view of an exhaust particulate treatment device showing a third embodiment of the present invention.

【図7】この発明の第4の実施例を示す排気微粒子処理
装置の断面図である。
FIG. 7 is a sectional view of an exhaust particulate treatment device showing a fourth embodiment of the present invention.

【図8】この発明の第5の実施例を示す排気微粒子処理
装置の断面図である。
FIG. 8 is a sectional view of an exhaust particulate treatment device showing a fifth embodiment of the present invention.

【図9】この発明の試験結果を示すフィルタ箱入口に対
する同出口の濃度変化率を、機関出力に応じて示した説
明図である。
FIG. 9 is an explanatory diagram showing test results of the present invention, showing the rate of change in concentration at the outlet of the filter box with respect to the inlet of the filter box, depending on the engine output.

【図10】この発明の試験結果を示す煤濃度を印加電圧
に応じて示した説明図である。
FIG. 10 is an explanatory diagram showing the test results of the present invention, showing the soot concentration according to the applied voltage.

【符号の説明】[Explanation of symbols]

1  排気通路 3  導電性吸着フィルタ(捕集部材)5  金網(導
電性部材) 7  直流電源(電圧印加手段)
1 Exhaust passage 3 Conductive adsorption filter (collection member) 5 Wire mesh (conductive member) 7 DC power supply (voltage application means)

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】  燃焼ガスが通過する排気通路に、燃焼
ガスに含まれる排気微粒子を捕集する導電性の捕集部材
を設け、この捕集部材の上流側の排気通路に、前記排気
微粒子を含む燃焼ガスが排気微粒子とともに通過可能な
導電性部材を設け、この導電性部材と前記捕集部材とに
互いに極性の異なる電荷を帯電させる電圧印加手段を設
けたことを特徴とする排気微粒子処理装置。
1. A conductive collection member for collecting exhaust particulates contained in the combustion gas is provided in an exhaust passage through which combustion gas passes, and the exhaust particulates are collected in an exhaust passage upstream of the collection member. An exhaust particulate processing device comprising: a conductive member through which combustion gases contained therein can pass together with the exhaust particulates; and voltage application means for charging the conductive member and the collection member with charges of different polarities. .
JP3064844A 1991-03-28 1991-03-28 Apparatus for treating fine particles in exhaust gas Pending JPH04300661A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3064844A JPH04300661A (en) 1991-03-28 1991-03-28 Apparatus for treating fine particles in exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3064844A JPH04300661A (en) 1991-03-28 1991-03-28 Apparatus for treating fine particles in exhaust gas

Publications (1)

Publication Number Publication Date
JPH04300661A true JPH04300661A (en) 1992-10-23

Family

ID=13269939

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3064844A Pending JPH04300661A (en) 1991-03-28 1991-03-28 Apparatus for treating fine particles in exhaust gas

Country Status (1)

Country Link
JP (1) JPH04300661A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006095429A (en) * 2004-09-29 2006-04-13 Sharp Corp Air cleaning device
JP2006194104A (en) * 2005-01-11 2006-07-27 Toyota Motor Corp Exhaust emission control device for internal combustion engine
US20120216674A1 (en) * 2009-09-14 2012-08-30 Emitec Gesellschaft Fuer Emissionstechnologie Mbh Device and method for treating exhaust gas containing soot particles
JP2014161760A (en) * 2013-02-22 2014-09-08 Mitsubishi Electric Corp Dehumidifier for apparatus and on-vehicle head lamp
JP2017051913A (en) * 2015-09-10 2017-03-16 春日電機株式会社 Dust collector

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006095429A (en) * 2004-09-29 2006-04-13 Sharp Corp Air cleaning device
JP4674071B2 (en) * 2004-09-29 2011-04-20 シャープ株式会社 Gas purifier
JP2006194104A (en) * 2005-01-11 2006-07-27 Toyota Motor Corp Exhaust emission control device for internal combustion engine
US20120216674A1 (en) * 2009-09-14 2012-08-30 Emitec Gesellschaft Fuer Emissionstechnologie Mbh Device and method for treating exhaust gas containing soot particles
JP2013504705A (en) * 2009-09-14 2013-02-07 エミテック ゲゼルシヤフト フユア エミツシオンス テクノロギー ミツト ベシユレンクテル ハフツング Apparatus and method for treating exhaust gas containing soot particles
US8747527B2 (en) * 2009-09-14 2014-06-10 Emitec Gesellschaft Fuer Emissionstechnologie Mbh Device and method for treating exhaust gas containing soot particles
US9157351B2 (en) 2009-09-14 2015-10-13 Emitec Gesellschaft Fuer Emissionstechnologie Mbh Method for treating exhaust gas containing soot particles
JP2014161760A (en) * 2013-02-22 2014-09-08 Mitsubishi Electric Corp Dehumidifier for apparatus and on-vehicle head lamp
JP2017051913A (en) * 2015-09-10 2017-03-16 春日電機株式会社 Dust collector

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