JPS6133626B2 - - Google Patents

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Publication number
JPS6133626B2
JPS6133626B2 JP9753177A JP9753177A JPS6133626B2 JP S6133626 B2 JPS6133626 B2 JP S6133626B2 JP 9753177 A JP9753177 A JP 9753177A JP 9753177 A JP9753177 A JP 9753177A JP S6133626 B2 JPS6133626 B2 JP S6133626B2
Authority
JP
Japan
Prior art keywords
dust
area
dust collection
electrode
transport
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.)
Expired
Application number
JP9753177A
Other languages
Japanese (ja)
Other versions
JPS5431677A (en
Inventor
Akira Yamauchi
Takao Komatsu
Jujiro Mimura
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.)
Sumitomo Metal Mining Co Ltd
Panasonic Ecology Systems Co Ltd
Original Assignee
Sumitomo Metal Mining Co Ltd
Matsushita Seiko 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 Sumitomo Metal Mining Co Ltd, Matsushita Seiko Co Ltd filed Critical Sumitomo Metal Mining Co Ltd
Priority to JP9753177A priority Critical patent/JPS5431677A/en
Publication of JPS5431677A publication Critical patent/JPS5431677A/en
Publication of JPS6133626B2 publication Critical patent/JPS6133626B2/ja
Granted legal-status Critical Current

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  • Electrostatic Separation (AREA)

Description

【発明の詳細な説明】 本発明は、電気集塵装置に関し、より詳細には
浮遊微粒子を含有する大風量の被処理気体を電気
集塵域に通過させて前記微粒子を該電気集塵域の
集塵電極上に捕集し、該集塵電極上の微粒子を凝
集した粗大粒子の形でしかも被処理気体よりも濃
厚な濃度の分散気流としてスムースに系外に搬出
して、該粗大粒子を過等の機械的集塵に賦する
ことによつて、比較的小さいスペースでしかも効
率よく、集塵、ダストの払い出し等の諸操作を行
い得る装置に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an electrostatic precipitator, and more specifically, the present invention relates to an electrostatic precipitator, and more specifically, a large amount of gas to be treated containing suspended fine particles is passed through an electrostatic precipitator area to collect the fine particles in the electrostatic precipitator area. The coarse particles are collected on the dust collection electrode, and are smoothly transported out of the system in the form of aggregated coarse particles with a concentration higher than that of the gas to be treated. The present invention relates to a device that can perform various operations such as collecting dust and discharging dust efficiently in a relatively small space by providing sufficient mechanical dust collection.

本発明の装置は、道路トンネルの空気の集塵操
作のように、微細粒子を稀薄な濃度で含有する気
体を大風量で取扱いしかも集塵域を限られた狭い
スペース内に設置して集塵やそれに付随する払い
出し操作を行わねばならない用途に特に有用であ
る。
The device of the present invention handles gas containing fine particles at a dilute concentration with a large air volume, like the air dust collection operation in road tunnels, and also installs the dust collection area in a narrow space to collect dust. This is particularly useful in applications where the dispensing operations associated with such dispensing operations must be performed.

道路トンネルには、自動車の走行に伴なつて排
出されるカーボン等の微粒子物質を含有する汚染
空気が滞留し、このような汚染空気は人体に対し
て健康上望ましくない影響を及ぼすのは勿論のこ
と、前記浮遊微粒子物質がトンネル内の視界を不
良とし、或いは照明器具等に沈着して照明の効率
を低下させる等の種々の不都合を生じる。
In road tunnels, polluted air containing particulate matter such as carbon emitted as vehicles travel accumulates, and it goes without saying that such polluted air has undesirable effects on human health. In addition, the suspended particulate matter causes various inconveniences such as poor visibility inside the tunnel or deposits on lighting equipment and the like, reducing the efficiency of lighting.

しかしながら、トンネル内の空気の集塵操作
は、空気中の浮遊粒子が微細でしかもその濃度が
著しく稀薄であること、大風量の処理気体を取扱
ねばならないこと、及び集塵装置の設置スペース
が限られた極く狭いスペースに限定されること等
の理由により多くの困難に遭遇する。
However, dust collection operations for the air in tunnels are difficult because suspended particles in the air are minute and extremely dilute, a large amount of gas must be handled, and the installation space for dust collectors is limited. Many difficulties are encountered due to reasons such as being confined to a very narrow space.

例えば、バツクフイルター等の過集塵方式
は、設置すべきスペースが比較的小さいという利
点を有しているが、微細な粒子に対する捕集効率
が低く、更に圧力損失が大きくて大風量の被処理
気体には明らかに適していない。一方、電気集塵
方式は、微細粒子の捕集効率が高く、また圧力損
失も比較的低く大風量の被処理気体の取扱いに適
しているという利点を有しているが、捕集した微
粒子(以下ダストとも呼ぶ)の払い出しが必らず
しも容易ではなく、更に設置スペースが大きくな
る等の欠点を有している。
For example, excessive dust collection methods such as back filters have the advantage of requiring a relatively small installation space, but they also have low collection efficiency for fine particles, have a large pressure loss, and require a large amount of air to be processed. Obviously not suitable for gases. On the other hand, the electrostatic precipitator method has the advantages of high collection efficiency for fine particles and relatively low pressure loss, making it suitable for handling large air volumes of gas. It is not always easy to remove the dust (hereinafter also referred to as dust), and it also has drawbacks such as requiring a large installation space.

即ち、電気集塵方式では、集塵電極上のダスト
の層が厚くなるとバツクコロナ現象等の電気的な
トラブルや、集塵効率の低下等のトラブルを生じ
ることになるので、捕集したダストを装置外部に
払い出すことが必要となるが、このダストの払い
出し操作は必らずしも容易ではない。このため
に、従来の商業的な電気集塵機においては、集塵
域の下方に大容量のホツパーを設け、集塵電極上
のダストを何等かの手段でホツパー内に払い落
し、ホツパー内に貯留されるダストを下部の排出
口から直接取り出すか或いはコンベヤー、搬送気
流等による搬送排出手段が講じられている(例え
ば特許第124181号明細書参照)。
In other words, in the electrostatic precipitator method, if the layer of dust on the precipitate electrode becomes thick, it will cause electrical problems such as back corona phenomenon and problems such as a decrease in dust collection efficiency. Although it is necessary to discharge the dust to the outside, this operation of discharging the dust is not necessarily easy. For this purpose, in conventional commercial electrostatic precipitators, a large-capacity hopper is installed below the dust collection area, and the dust on the dust collection electrode is brushed off into the hopper by some means, and the dust is stored in the hopper. The dust is taken out directly from the lower discharge port, or conveyance and discharge means are used such as a conveyor or a conveying air current (see, for example, the specification of Japanese Patent No. 124181).

しかしながら、このような排出機構では、装置
全体のスペース当りの集塵操作に有効な部分のス
ペースの比、即ち占積率が非常に小さく、またホ
ツパー内に堆積した粉塵がブリツジ現象を起して
粉集塵の排出不良というトラブルが発生し易く、
更にホツパーの上部に重量の有る電気集塵機本体
を設置しなければならない等、構造上改善すべき
問題点を未だ有している。
However, in such a discharge mechanism, the ratio of the space effective for dust collection operation to the space of the entire device, that is, the space factor, is very small, and the dust accumulated in the hopper may cause a bridging phenomenon. Troubles such as poor discharge of dust collection are likely to occur.
Furthermore, there are still structural problems that need to be improved, such as the need to install a heavy electrostatic precipitator body above the hopper.

本発明者等は、気体中の浮遊微粒子を電気集塵
域で集塵電極上に捕集する操作と、該集塵電極へ
圧搾空気を変動流として吹付けて捕集粉塵を払い
落すと同時に、この払い落される凝集粗大粒子を
直接電気集塵域の下方全域を流れる層状の搬送気
流中に濃厚な形で再分散させて電気集塵域外に排
出する操作とこの搬送気流を再び過等の機械的
集塵に賦して搬送気流中から凝集粗大粒子を分離
する操作とを組合せるときには、比較的小さなス
ペース内でしかも効率よく、微細粒子の捕集と払
い出しを行い得ることを見出した。
The present inventors conducted an operation to collect suspended particulates in a gas onto a dust collecting electrode in an electrostatic precipitating area, and simultaneously blew off the collected dust by blowing a fluctuating flow of compressed air onto the dust collecting electrode. The aggregated coarse particles that are brushed off are redispersed in a concentrated form into the laminar carrier airflow that flows directly below the electrostatic precipitator area, and are then discharged outside the electrostatic precipitator area. It has been found that when mechanical dust collection is combined with the operation of separating aggregated coarse particles from the conveying air stream, fine particles can be efficiently collected and discharged within a relatively small space. .

本発明の目的は、浮遊微細粒子を稀薄な濃度で
含有する大風量の気体からの電気集塵、電気集塵
域からの粉塵の払い落し及び払い出し、及び粉塵
の回収を狭いスペース内で効率よく、短時間に行
うことが可能な電気集塵装置を提供するにある。
The purpose of the present invention is to efficiently collect dust from a large volume of gas containing suspended fine particles at a dilute concentration, to blow off and blow out dust from an electrostatic collection area, and to collect dust efficiently in a narrow space. The object of the present invention is to provide an electrostatic precipitator that can be used in a short period of time.

本発明の他の目的は、装置全体のスペース当り
の集塵操作に有効な部分のスペースの比、即ち占
積率が公知の電気集塵装置に比して著しく高い電
気集塵装置を提供するにある。
Another object of the present invention is to provide an electrostatic precipitator that has a ratio of space effective for dust collection operations per space of the entire device, that is, a space factor that is significantly higher than that of known electrostatic precipitators. It is in.

本発明に更に他の目的は、粉塵の排出不良とい
うトラブルを発生することなく、安定して連続し
た集塵操作を行い得る電気集塵装置を提供するに
ある。
Still another object of the present invention is to provide an electrostatic precipitator that can perform stable and continuous dust collection operations without causing problems such as poor dust discharge.

本発明の更に他の目的は、集塵電極面へ圧搾空
気を変動流として吹付けて捕集粉塵を効率良く払
い落すと同時に、この払い落された粉塵を電気集
塵域の直下に形成された層状の搬送気流中に乗せ
て装置外へ排出することにより、捕集粉塵の装置
外への払い出しが円滑にしかも短時間で行い得る
電気集塵装置を提供するにある。
Still another object of the present invention is to efficiently blow off the collected dust by blowing compressed air as a fluctuating flow onto the surface of the dust collecting electrode, and at the same time, to form the dust that has been blown off directly under the electrostatic precipitate area. An object of the present invention is to provide an electrostatic precipitator in which collected dust can be smoothly discharged outside the device in a short period of time by being carried in a laminar carrier air flow and being discharged outside the device.

本発明の更に他の目的は、トンネル内の集塵操
作に特に適した電気集塵装置を提供するにある。
Yet another object of the invention is to provide an electrostatic precipitator particularly suitable for dust collection operations in tunnels.

本発明によれば、集塵電極及び対極を備えた電
気集塵域、集塵域下方に位置し且つこれと直接連
通するダスト搬送域、集塵域の入口及び出口を集
塵操作時に開き且つこれらをダスト搬送時に閉塞
するための開閉機構、集塵電極上の付着ダストを
ダスト搬送域に払い落すための乾式ダスト払い落
し機構、前記ダスト搬送域に搬送気流を供給し且
つダストを分散物の形でダスト搬送域外に排出乃
至吸引するための送排風機構、及び前記送排風機
構の排出乃至吸引側に設けられた機械的集塵域か
ら成る電気集塵装置において、前記乾式ダスト払
い落し機構は、集塵電極面へ付着ダスト払い落し
用の圧搾空気を噴射する噴射ノズルと、該噴射ノ
ズルを左右に平行移動させしかも上下に首振り運
動させる機構を備えており、且つ前記ダスト搬送
域は、前記電気集塵域と実質的に同一の設置面積
を有しており、且つダスト排出時には該ダスト搬
送域の全域に亘つて層状で一定方向のダスト搬送
気流が形成されるようになされており、圧搾空気
の吹付けにより払い落されるダストがダスト搬送
域のダスト搬送気流に乗せられて機械的集塵域に
排出されるように関連されていることを特徴とす
る電気集塵装置が提供される。
According to the present invention, an electric dust collection area equipped with a dust collection electrode and a counter electrode, a dust transport area located below the dust collection area and directly communicating therewith, and an inlet and an outlet of the dust collection area that are opened during a dust collection operation and An opening/closing mechanism for closing these during dust transport, a dry dust removal mechanism for brushing off the dust adhering to the dust collection electrodes into the dust transport area, and a dry dust removal mechanism for supplying a transport airflow to the dust transport area and dispersing the dust. In an electrostatic precipitator comprising an air blowing/exhausting mechanism for discharging or suctioning dust out of a dust conveying area in a shape, and a mechanical dust collecting area provided on the exhausting or suction side of the air blowing/exhausting mechanism, the dry dust removal method The mechanism includes an injection nozzle that injects compressed air for brushing off dust adhering to the dust collection electrode surface, and a mechanism that moves the injection nozzle in parallel from side to side and oscillates up and down. has substantially the same installation area as the electrostatic precipitator area, and is configured to form a layered dust conveying airflow in a constant direction over the entire area of the dust conveying area during dust discharge. An electrostatic precipitator is characterized in that the dust collected by blowing compressed air is carried by the dust conveying airflow of the dust conveying zone and discharged to the mechanical dust collecting zone. provided.

本発明の装置は、浮遊微細粒子を含有する任意
の気体に対して適用可能であるが、このような浮
遊粒子は、集塵電極から圧搾空気を用いて乾式で
払い落すこと、及びその再分散物を過、遠心、
慣性等の機械的集塵に賦すことに関連して、これ
らの操作条件下で非粘着性、即ち固体であること
が必要である。勿論、これらの浮遊微細粒子中に
は、タール等の粘着性成分が含有されていても、
全体として捕集した粉塵が非粘着性の状態に保持
されていれば、本発明の処理に適用することがで
きる。微細粒子の種類も、特に制限はなく、自動
車等の排気ガス中に含まれるカーボンのように導
電性のものから、アツシユ(灰分)、無機酸化物
等の比較的低導電性のもの迄、広範囲のものであ
つてよい。
Although the device of the present invention is applicable to any gas containing suspended fine particles, such suspended particles can be removed by dry blowing off the dust collection electrode using compressed air, and their redispersion. passing things through, centrifuging,
In connection with application to mechanical dust collection, such as inertia, it is necessary to be non-stick, ie solid, under these operating conditions. Of course, even if these suspended fine particles contain sticky components such as tar,
As long as the collected dust is kept in a non-stick state as a whole, it can be applied to the treatment of the present invention. There are no particular restrictions on the type of fine particles, and they can range from conductive ones such as carbon contained in automobile exhaust gas to relatively low conductive ones such as ash and inorganic oxides. It may be something like that.

浮遊微細粒子の粒径も特に制限はないが、特に
粒径が1ミクロン(μ)よりも小さい微粒子を
も、高速の気流から容易に除去し得ることが本発
明の利点である。被処理気体中に含有される浮遊
微細粒子の濃度も広範囲に変化してもよいが、本
発明の装置は、トンネル内に充満する自動車排気
ガスのように、粉塵濃度が0.1乃至10mg/m3のよう
に比較的稀薄な気体の処理にも有効に使用し得
る。
Although there is no particular restriction on the particle size of the suspended fine particles, it is an advantage of the present invention that even fine particles having a particle size of less than 1 micron (μ) can be easily removed from a high-speed airflow. Although the concentration of suspended fine particles contained in the gas to be treated may vary over a wide range, the apparatus of the present invention is suitable for use when the dust concentration is between 0.1 and 10 mg/m 3 , such as automobile exhaust gas filling a tunnel. It can also be effectively used to treat relatively dilute gases such as.

電気集塵域としては、集塵電極と対極とから成
るそれ自体公知の任意の電気集塵機構が使用され
る。大風量の被処理気体を、比較的小さなスペー
スの電気集塵域で処理するためには、電気集塵域
の圧力損失を少なくし且つ高速で被処理気体を通
過させることが一般に必要であり、かかる見地か
らは、集塵電極と対極との対が被処理気体の進行
方向に延びて電気集塵用通路を形成していること
が望ましい。一般には、複数個の集塵電極と対極
とを交互に設けて、気体の進行方向に多数の電気
集塵用通路を形成させることが高速気流からの微
細粒子の分離捕集を有効に行わせるために好適で
ある。
As the electrostatic precipitator area, any electrostatic precipitator mechanism known per se, consisting of a precipitator electrode and a counter electrode, can be used. In order to process a large amount of gas to be treated in an electrostatic precipitator area with a relatively small space, it is generally necessary to reduce the pressure loss in the electrostatic precipitator area and to allow the gas to pass through at high speed. From this point of view, it is desirable that the pair of the dust collection electrode and the counter electrode extend in the direction of movement of the gas to be treated to form an electrical dust collection passage. In general, it is effective to separate and collect fine particles from high-speed airflow by alternately providing a plurality of dust collection electrodes and counter electrodes to form a large number of electrostatic collection passages in the direction of gas movement. It is suitable for

集塵電極は、普通の板状電極でよいが、所望に
よつては金網、メタルラス等の多孔性の金属部材
でも使用し得る。対極としては、コロナワイヤ
ー、その他の尖鋭化電極、棒状電極、板状電極或
いはこれらの組合せを使用し得る。
The dust collecting electrode may be an ordinary plate-shaped electrode, but if desired, a porous metal member such as a wire mesh or metal lath may also be used. As the counter electrode, a corona wire, other sharpened electrode, rod-shaped electrode, plate-shaped electrode, or a combination thereof can be used.

電気集塵通路内で浮遊微細粒子の荷電と捕集と
を同時に行うことも、或いは電気集塵通路の上流
側で前記粒子の荷電を行い、電気集塵通路内では
荷電粒子の捕集のみを行わせることもできる。前
者の場合には、対極としてコロナワイヤ、尖鋭化
電極等のコロナ発生能を有する電極、或いはコロ
ナ発生能を有する電極と棒状電極、板状電極等の
コロナ発生能を有しない電極との組合せが使用さ
れる。また、後者の場合には、電気集塵通路の上
流側にコロナ発生能を有する電極、即ち荷電電極
或いは荷電電極と接地電極(例えば金網)との対
を設け、電気集塵通路の対極としてはコロナ発生
能を有しない電極を用いる。
It is possible to simultaneously charge and collect suspended fine particles in the electrostatic precipitator passage, or to charge the particles on the upstream side of the electrostatic precipitator passage and collect only the charged particles in the electrostatic precipitator passage. You can also make it happen. In the former case, the counter electrode may be an electrode with corona-generating ability such as a corona wire or a sharpened electrode, or a combination of an electrode with corona-generating ability and an electrode without corona-generating ability such as a rod-like electrode or a plate-like electrode. used. In the latter case, an electrode capable of generating corona, that is, a charged electrode, or a pair of a charged electrode and a ground electrode (for example, a wire mesh) is provided on the upstream side of the electrostatic precipitator passage, and as a counter electrode of the electrostatic precipitate passage. Use electrodes that do not have the ability to generate corona.

対極と捕集電極との間隙は種々変化させ得る
が、一般には5乃至60mm程度の間隙のもの(以
後、狭極間粉塵通路と呼ぶことがある)が特に好
適である。しかしながら、この間隙は、勿論60mm
以上に拡げることも可能である。電気集塵通路の
長さも種々変化させ得るが、前述した狭極間集塵
通路の場合には10cm乃至500cmの範囲で十分であ
る。
Although the gap between the counter electrode and the collection electrode can be varied, a gap of about 5 to 60 mm (hereinafter sometimes referred to as a narrow interelectrode dust passage) is particularly suitable. However, this gap is of course 60mm.
It is also possible to expand beyond this. Although the length of the electrostatic precipitate passage can be varied, a range of 10 cm to 500 cm is sufficient in the case of the narrow inter-electrode dust collection passage described above.

対極と捕集電極間に印加する電圧は、捕集のみ
を対象とするか、或いは荷電と捕集の両者を対象
とするかによつても、或いは両者の極間距離によ
つても相違するが、平均電位勾配が一般に1.5乃
至12kV/cmの範囲となるように、適当な電圧を選
ぶことが好ましい。
The voltage applied between the counter electrode and the collection electrode differs depending on whether only collection is targeted, or both charging and collection are targeted, or depending on the distance between the two electrodes. However, it is preferable to choose an appropriate voltage such that the average potential gradient is generally in the range of 1.5 to 12 kV/cm.

本発明において、電気集塵域内に通じる被処理
気体の流速も広範囲に変化できるが、前述した狭
極間集塵通路を用いる場合には、被処理気体の線
流速を3m/sec以上のような高速にして、浮遊微
細粒子の捕集を有効に行なうことができる。
In the present invention, the flow velocity of the gas to be treated leading into the electrostatic precipitator region can be varied over a wide range, but when using the narrow inter-electrode dust collection passage described above, the linear flow velocity of the gas to be treated can be set to 3 m/sec or more. At high speed, floating fine particles can be collected effectively.

本発明の重要な特徴は、大風量の被処理気体を
圧力損失の小さい電気集塵域に供給して、微細粒
子の捕集を行い、一方電極から圧搾空気変動流の
吹付けにより払い落される粒子を払い落し操作と
同時に電気集塵域の下方全域に形成される小風量
の層状搬送気流に乗せて払い出し、過、遠心、
慣性等の機械的集塵に賦することに存する。
An important feature of the present invention is that fine particles are collected by supplying a large volume of the gas to be treated to an electrostatic precipitator area with low pressure loss, while the fine particles are blown away from the electrodes by blowing a fluctuating flow of compressed air. At the same time as the dust removal operation, the particles are swept away by a small air volume laminar conveying airflow that is formed in the entire lower part of the electrostatic precipitator area,
It consists in applying mechanical dust collection such as inertia.

即ち、捕集電極上に沈着した前記微細粒子は、
凝集粗大化されており、圧搾空気変動流の吹付け
により捕集電極上から払い落してその下方全域に
形成された小風量の層状搬送気流によつて払い出
し過等の機械的集塵域に移送すると、高い回収
効率でしかも比較的小容積の付属設備で、捕集粉
塵の払い出し及び回収が有効に行われることにな
る。かくして、本発明によれば、前述した占積率
を公知の電気集塵方式に比して著しく高くして装
置を限られた狭いスペースに設置することが可能
となり、更に捕集粉塵の払い出しや回収操作をも
一層容易にすることが可能となる。
That is, the fine particles deposited on the collection electrode are
The particles are aggregated and coarsened, and are blown off from above the collection electrode by the fluctuating flow of compressed air, and then transferred to a mechanical dust collection area such as a dust collection area by a laminar conveying air flow with a small air volume formed over the entire area below. As a result, the collected dust can be effectively discharged and collected using attached equipment with high collection efficiency and relatively small volume. Thus, according to the present invention, the above-mentioned space factor is significantly higher than that of the known electrostatic precipitator method, making it possible to install the device in a limited narrow space, and furthermore, it is possible to dispose of the collected dust and It also becomes possible to further facilitate the collection operation.

このため本発明によれば、捕集電極上に付着し
たダストの乾式払い落し機構として、捕集電極面
へ付着ダスト払い落し用の圧搾空気を噴射する噴
射ノズルと、該噴射ノズルを左右に平行移動させ
しかも上下に首振り運動をさせる機構とを備えた
ものを採用した。即ちこれらの機構を採用するこ
とにより、捕集電極面上への圧搾空気の噴射が変
動流として行なわれるので、捕集電極面上に満遍
なく圧搾空気の噴射が行なわれるばかりではな
く、空気の噴射された部分から順次ダストの払い
落しが行なわれることから、少ない風量で継続し
たダストの払い落しとダストの排出とが安定にし
かも円滑に可能となるのである。
Therefore, according to the present invention, as a dry-type dust removal mechanism for dust adhering to the collection electrode, there is provided an injection nozzle that injects compressed air for removing the adhering dust onto the collection electrode surface, and the injection nozzle is arranged in parallel to the left and right. We adopted a device equipped with a mechanism that allows it to be moved and also to oscillate up and down. In other words, by adopting these mechanisms, the injection of compressed air onto the surface of the collection electrode is performed as a fluctuating flow, so that not only is the injection of compressed air evenly distributed over the surface of the collection electrode, but also the injection of air is Since the dust is sequentially removed from the area where the dust has been removed, it is possible to stably and smoothly continue removing the dust and discharging the dust with a small amount of air.

また本発明によれば、電気集塵域の下方に直接
これと連通し且つ該電気集塵域と実質的に同一の
設置面積を有するダスト搬送域を設け、このダス
ト搬送域の全域に亘つて層状で一定方向に流れる
ダスト搬送気流を形成させ、この搬送気流を電気
集塵域外の別の機械的集塵域等に連通するように
した。即ちこれにより捕集電極から払い落される
ダストは装置本体に貯留されることなく直ちに機
械的集塵域に排出されるのであり、また層状で一
定方向の搬送気流を形成させるため、比較的少な
い風量の搬送気流でダストの排出を円滑に行なう
ことが可能となるものである。
Further, according to the present invention, a dust transport area is provided below the electrostatic precipitator area and is in direct communication with the electrostatic precipitator area and has substantially the same installation area as the electrostatic precipitator area. A layered dust transporting airflow flowing in a fixed direction is formed, and this transporting airflow is communicated with another mechanical dust collection area outside the electrostatic dust collection area. In other words, the dust that is brushed off from the collection electrode is immediately discharged to the mechanical dust collection area without being stored in the main body of the device, and because it forms a layered and unidirectional conveying airflow, there is relatively little dust. This makes it possible to smoothly discharge dust by using a conveying air flow with a large amount of air.

また更に本発明においては、前記付着ダストの
払い落しと、この払い落されたダストの電気集塵
域外への排出とを同時に行なうようにした。即ち
これにより、大容量のホツパーの設置が不要とな
り、装置全体のスペース当りの集塵操作に有効な
部分のスペースの比、即ち占積率を従来のものに
比して著しく大きな値とし、装置の設置容積等が
著しく制限されるトンネル内集塵の用途にも使用
可能にしたものである。
Furthermore, in the present invention, the above-mentioned dust removal is simultaneously performed and the dust thus removed is discharged outside the electrostatic precipitating area. In other words, this eliminates the need to install a large-capacity hopper, and increases the ratio of the space effective for dust collection operations to the space of the entire device, that is, the space factor, to a significantly larger value compared to conventional ones. This makes it possible to use it for dust collection in tunnels, where installation volume is severely limited.

本発明における、圧搾空気の吹付けはそれ自体
公知の方法で行なうことができ、例えば、エアコ
ンプレツサー、ブロワー、フアン等を使用して行
なうことができる。
In the present invention, the blowing of compressed air can be carried out by a method known per se, for example, by using an air compressor, blower, fan, etc.

捕集粉塵を払い落す場合には、粉塵を乾いた状
態で払い落すことが特に重要であり、水膜や水噴
射等を用いて捕集粉塵をスラリーの状態で払い落
すときには、このスラリーの輸送や、スラリーか
らの粉塵の回収に多くの問題を生じる。
When removing collected dust, it is especially important to remove the dust in a dry state.When removing collected dust in the form of a slurry using a water film or water jet, transportation of this slurry is particularly important. This creates many problems in collecting dust from the slurry.

ダスト搬送域の寸法は、電気集塵域に対応する
面積を有し且つ払い落されるダストを搬送気流に
載せて移動させ得る高さを有していれば十分であ
るから、前述したホツパ等に比べればその設置寸
法は極めて微々たるものである。尚、所望によつ
ては電気集塵域とダスト搬送時との間にパンチン
グメタル、金網等の多孔性部材を設けてもよい。
The dimensions of the dust transport area are sufficient as long as they have an area corresponding to the electrostatic precipitate area and a height that allows the dust to be brushed off to be carried on the transport airflow and moved. Its installation size is extremely small compared to . If desired, a porous member such as punched metal or wire mesh may be provided between the electrostatic precipitate collection area and the dust transport area.

特に、本発明によれば、ダスト搬送域は低い高
さで十分であると共にダスト含有搬送気体の排出
口は横方向に設置できるため、電気集塵域とダス
ト搬送域とをユニツトの形で多段に積重してスペ
ースを無駄なく使用することができること、及び
従来のホツパー等のダスト排出機構に比してデツ
ドスペースが殆んどないことも顕著な利点であ
る。
In particular, according to the present invention, a low height is sufficient for the dust transport area, and the exhaust port for the dust-containing transport gas can be installed in the horizontal direction. Another notable advantage is that the dust can be stacked on top of each other so that space can be used without wasting space, and that there is almost no dead space compared to conventional dust ejection mechanisms such as hoppers.

本発明によれば、払い落されるダストを搬送気
流中に分散させてこのダストを前述した被処理気
体よりも濃厚な濃度で含有する分散物(懸濁気
体)とし、この分散物を過等の機械的集塵域に
移送する。
According to the present invention, the dust to be brushed off is dispersed in a conveying air stream to form a dispersion (suspended gas) containing this dust at a concentration higher than that of the above-mentioned gas to be treated, and this dispersion is Transfer to mechanical dust collection area.

このために、前述したダスト搬送域の一方の側
に搬送気体の供給口及び他方の側に分散気体の排
出口を設ける。
For this purpose, a supply port for the carrier gas is provided on one side of the dust transfer area and a discharge port for the dispersion gas is provided on the other side.

ダストの払い落し及び払い落されたダストの気
流搬送に際して、ダストが電気集塵域外に飛散す
ること及び余剰空気の流入等を防止するために、
電気集塵域の入口及び出口に夫々開閉機構を設
け、払い落し操作及び気流搬送操作時にこれらの
開閉機構を閉じるようにする。
In order to prevent the dust from scattering outside the electrostatic precipitator area and the inflow of excess air when dust is removed and the removed dust is transported by airflow,
An opening/closing mechanism is provided at the inlet and outlet of the electrostatic precipitating area, and these opening/closing mechanisms are closed during the dusting operation and air flow conveyance operation.

搬送気体中のダスト濃度は、種々変化させ得る
が、一般には被処理ガス中の濃度の数倍乃至数千
倍のオーダーの範囲にあるのが、能率とスペース
縮少の見地から望ましく、上記濃度を維持するの
に必要な搬送気体を供給するのがよい。
The dust concentration in the carrier gas can be varied in various ways, but it is generally desirable to have it in the range of several times to several thousand times the concentration in the gas to be treated from the standpoint of efficiency and space reduction. It is advisable to supply the necessary carrier gas to maintain the

搬送気体をダスト搬送域に供給するのには、前
記供給口から搬送気体を圧送する方式、及び前記
排出口からダスト分散搬送気体を吸引し且つこれ
に見合う搬送気体を供給口からダスト搬送域に通
風させる方式の何れをも採用し得る。圧送式の場
合には、前記供給口としてスリツト状或いはその
他の形状のノズルを使用してもよい。
In order to supply the carrier gas to the dust transport area, there is a method of pumping the carrier gas from the supply port, sucking the dust dispersion transport gas from the discharge port, and supplying a corresponding amount of transport gas from the supply port to the dust transport area. Any method of ventilation may be adopted. In the case of a pressure feeding type, a slit-shaped or other shaped nozzle may be used as the supply port.

本発明によれば、かくして捕集電極から払い落
されるダストは、搬送気体に載せられて迅速に機
械的集塵域に導かれ、ダストの払い出しとダスト
の分離回収とが極めて短時間に行なわれることも
本発明の利点の一つである。機械的集塵域として
は、バツグフイルター等の過集塵、サイクロ
ン、機械的遠心集塵装置等の遠心集塵、ルーバ式
集塵機等の慣性集塵、或いはこれらの組合せを使
用することができ、これら何れの場合にも、ダス
トが十分な大きさに凝集粗大化していること、及
びダストの濃度が高く且つこれに伴なつて風量が
小さいことに関連して、比較的小さなスペースで
効率よくダストの分離及び回収を行なうことがで
きる。
According to the present invention, the dust thus brushed off from the collection electrode is carried on the carrier gas and quickly guided to the mechanical dust collection area, and the dust dust is removed and separated and collected in an extremely short time. It is also one of the advantages of the present invention. As the mechanical dust collection area, excessive dust collection such as a bag filter, centrifugal dust collection such as a cyclone, mechanical centrifugal dust collector, inertial dust collection such as a louver dust collector, or a combination thereof can be used. In any of these cases, dust can be efficiently removed in a relatively small space due to the fact that the dust has aggregated to a sufficiently large size, and the dust concentration is high and the air volume is accordingly small. can be separated and recovered.

更に、本発明によれば、電気集塵操作を行なう
時間に比して、ダストの払い落し及び払い出しに
必要な時間は著しく短かい時間であり、例えば捕
集すべき浮遊微細粒子が自動車排気ガス等のカー
ボン質のものである場合、前者が12乃至48時間で
あるのに対して、後者が1乃至3分間の時間であ
つて装置の遊び時間が著しく短かいことも了解さ
れよう。
Further, according to the present invention, the time required for dust removal and discharging is significantly shorter than the time required to perform an electrostatic precipitator operation. It will also be understood that in the case of a carbonaceous material such as, the idle time of the device is extremely short, with the former being 12 to 48 hours, while the latter is 1 to 3 minutes.

本発明によれば、電気集塵操作と捕集ダストの
払い落し及び払い出し操作とは交互に行なわれる
ことに関連して、複数個の電気集塵域を設け、一
つの集塵域において捕集ダストの払い落し及び払
い出し操作を行なうときには、他の電気集塵域に
おいて電気集塵操作を行なうようにすることが好
ましい。
According to the present invention, in connection with the fact that the electrostatic precipitate operation and the dust removal and discharging operations are performed alternately, a plurality of electrostatic precipitate areas are provided, and the dust is collected in one dust collection area. When performing the dust dust removal and discharging operations, it is preferable to perform the electrostatic precipitating operation in another electrostatic precipitating area.

以下に本発明の一実施例を添付図面に基づいて
詳細に説明する。
An embodiment of the present invention will be described in detail below with reference to the accompanying drawings.

第1図は、トンネル(図示せず)内を走行する
自動車(図示せず)より排出されるダスト(主と
して固形炭素、灰)を処理するに最適な電気集塵
装置の一部系統的説明図であつて、該装置の特徴
は、集塵電極1及び対極2を備えた集塵域3と、
該集塵域3の下方に位置し且つこれと直接連通す
るダスト搬送域4と、前記集塵域3の入口5及び
出口6を集塵操作時に開き且つこれらをダスト搬
送時に閉塞するための開閉機構7a,7bと、前
記集塵電極1上の付着ダストをダスト搬送域4に
払い落すための乾式ダスト払い落し機構8と、前
記ダスト搬送域4に搬送気流を供給し、且つダス
トを分散物の形でダスト搬送域4外に排出するた
めの送排風機構9及び該送排風機構9の吸引側に
連通する過集塵域10とで構成される電気集塵
装置において、前記乾式ダスト払い落し機構8
が、集塵電極1及び対極2へ付着ダスト払い落し
用の圧搾空気を噴射する噴射ノズル16と、該噴
射ノズル16を左右に平行移動させしかも上下に
首振り運動させる機構27,36を備えており、
且つ前記ダスト搬送域4は、前記電気集塵域3と
実質的に同一の設置面積を有しており、且つダス
ト排出時には該ダスト搬送域4の全域に亘つて層
状で一定方向のダスト搬送気流が形成されるよう
になされており、圧搾空気の吹付けにより払い落
されるダストがダスト搬送域4のダスト搬送気流
に乗せられて機械的集塵域10に排出されるよう
に関連されていることにある。
Figure 1 is a partial systematic explanatory diagram of an electrostatic precipitator that is most suitable for treating dust (mainly solid carbon and ash) discharged from automobiles (not shown) running in tunnels (not shown). The features of the device include a dust collection area 3 equipped with a dust collection electrode 1 and a counter electrode 2;
A dust conveyance area 4 located below and directly communicating with the dust collection area 3, and an opening/closing mechanism for opening the inlet 5 and outlet 6 of the dust collection area 3 during dust collection operation and closing them during dust conveyance. Mechanisms 7a and 7b, a dry dust removal mechanism 8 for blowing off the dust adhering on the dust collection electrode 1 to the dust transport area 4, and a dry dust removal mechanism 8 for supplying a transport airflow to the dust transport area 4 and dispersing the dust. In an electrostatic precipitator comprising an air blowing/discharging mechanism 9 for discharging dust outside the dust conveying area 4 in the form of Brushing mechanism 8
is equipped with an injection nozzle 16 for injecting compressed air for removing adhering dust to the dust collecting electrode 1 and counter electrode 2, and mechanisms 27 and 36 for moving the injection nozzle 16 in parallel from side to side and swinging it up and down. Ori,
Further, the dust transport area 4 has substantially the same installation area as the electrostatic precipitator area 3, and when discharging dust, there is a layered dust transport airflow in a constant direction over the entire area of the dust transport area 4. is formed, and the dust that is blown off by the blowing of compressed air is carried by the dust transport airflow of the dust transport area 4 and is discharged to the mechanical dust collection area 10. There is a particular thing.

通常、前記集塵電極1と対極2とは、10乃至80
mm程度の間隔で複数個並設され、これによつて集
塵域3が形成される。
Usually, the dust collecting electrode 1 and the counter electrode 2 have a diameter of 10 to 80
A plurality of them are arranged in parallel at intervals of about mm, thereby forming a dust collection area 3.

本実施例における前記対極2は、集塵電極1を
同様な平板を用いていることから、該対極2のガ
ス導入側の端部は積極的なコロナ放電が発生する
ように尖鋭化されている。
Since the counter electrode 2 in this embodiment uses a flat plate similar to the dust collecting electrode 1, the end of the counter electrode 2 on the gas introduction side is sharpened to generate active corona discharge. .

無論、本発明の装置においての前記コロナ放電
の発生手段は何等該手段に限定されるものでな
く、各種の公知手段が任意に採用し得る。
Of course, the means for generating the corona discharge in the apparatus of the present invention is not limited to these means, and various known means may be arbitrarily employed.

なお、前記対極2は、その正常運転時8乃至
15kV程度の高電圧が高電圧供給ケーブル11を
介して高電圧発生装置12より供給されている。
Note that the counter electrode 2 has a temperature of 8 to 8 during normal operation.
A high voltage of about 15 kV is supplied from a high voltage generator 12 via a high voltage supply cable 11.

しかして、トンネル(図示せず)内を走行する
自動車より排出されるダストを含有した気体は、
該トンネルに連通するダスト含有気体導入通路1
3を介して前記集塵域3に供給されて電気的に処
理される。
Therefore, the dust-containing gas discharged from a car traveling in a tunnel (not shown) is
Dust-containing gas introduction passage 1 communicating with the tunnel
3 to the dust collection area 3 and electrically processed.

このダスト含有気体の電気的処理において、常
時高い捕集効率を維持するためには、すでに知ら
れているように、前記集塵域3を形成する集塵電
極1と対極2とに経時と共に付着するダストを適
宜に除去することが必要である。
In this electrical treatment of dust-containing gas, in order to maintain high collection efficiency at all times, as is already known, it is necessary to adhere to the dust collection electrode 1 and the counter electrode 2 that form the dust collection area 3 over time. It is necessary to remove the dust as appropriate.

本実施例におけるこれら付着ダストの除去は、
該付着ダストが非粘着性物質であることに着目し
て変動する噴射気体流で行つている。
The removal of these attached dust in this example is as follows:
Taking note of the fact that the adhering dust is a non-adhesive substance, this is carried out using a fluctuating jet gas flow.

該噴射気体流の形成は、圧搾空気供給源14に
圧搾空気供給管15を介して連通される乾式ダス
ト払い落し機構8によつて行われる。
The formation of the jet gas stream is carried out by a dry dust-off mechanism 8 which communicates with a compressed air supply source 14 via a compressed air supply pipe 15 .

本実施例における該乾式ダスト払い落し機構8
は、集塵通路3の数が考慮されて複数個並設され
る噴射ノズル16を備えるパイプ17によつて構
成されている。
The dry dust removal mechanism 8 in this embodiment
is constituted by a pipe 17 having a plurality of injection nozzles 16 arranged in parallel in consideration of the number of dust collection passages 3.

通常、上記構成から成る乾式ダスト払い落し機
構8は、少なくとも一段以上適宜に離隔して配設
される。
Normally, the dry dust removal mechanism 8 having the above-mentioned configuration is arranged at least one stage or more apart from each other as appropriate.

本実施例の如く、前記乾式ダスト払い落し機構
8を四段とした場合には、最少の噴射気流量で有
効かつ効果的にダストを払い落すために、各段に
圧搾空気流を分配供給するための分配供給管18
に電磁弁19を配設し、これによつて噴射気体流
の形成を選択制御することが好ましい。
When the dry dust blowing mechanism 8 has four stages as in this embodiment, compressed air flow is distributed and supplied to each stage in order to effectively and effectively blow off dust with the minimum amount of jet air flow. Distribution supply pipe 18 for
Preferably, a solenoid valve 19 is disposed at , by means of which the formation of the injection gas flow is selectively controlled.

また、前記最少の噴射気流量で有効かつ効果的
にダストを払い落すためには、前記手段に更にノ
ズル部を回動自在にすることが重要である。
Furthermore, in order to effectively and effectively blow off dust with the minimum amount of jet air, it is important that the nozzle part of the means is further rotatable.

なお上記付着ダストの操作時は、集塵域3への
ダスト含有気体の供給が、前記開閉機構7a,7
bによつて遮断される。
Note that when operating the attached dust, the dust-containing gas is supplied to the dust collection area 3 by the opening/closing mechanisms 7a, 7.
blocked by b.

本実施例における開閉機構7a,7bは、シリ
ンダー20を備えた扉21によつて構成される。
The opening/closing mechanisms 7a and 7b in this embodiment are constituted by a door 21 provided with a cylinder 20.

無論、該開閉機構7a,7bの構成はこれに限
定されるものではなく、例えばトンネル内で形成
されるダスト含有気体をダストを介して供給する
場合には、ダンパーを設けることによつても行
え、その選択はダスト含有気体の導入条件を考慮
して決定すれば良い。
Of course, the configuration of the opening/closing mechanisms 7a and 7b is not limited to this, and for example, if the dust-containing gas formed in the tunnel is to be supplied via dust, a damper may also be provided. , the selection thereof may be determined by considering the introduction conditions of the dust-containing gas.

かくして、集塵域3が密閉された状態で噴射気
体流によつて払い落されたダストは、集塵域3の
下方に位置しかつこれと連通するダスト搬送域4
に落下し、該ダスト搬送域4内に供給される搬送
気流中に分散せしめられる。
In this way, the dust that is blown off by the jet gas flow while the dust collection area 3 is sealed is transferred to the dust transport area 4 that is located below the dust collection area 3 and communicates with it.
The dust particles fall into the dust transport area 4 and are dispersed in the transport airflow supplied into the dust transport area 4.

なお、集塵電極1および対極2から噴射気体流
によつて払い落されるダストは凝集粗大化作用に
より、その発生時のものと較べ著しく粗大化され
ている。
It should be noted that the dust that is blown off from the dust collection electrode 1 and the counter electrode 2 by the jetted gas flow is significantly coarsened compared to when it was generated due to the agglomeration and coarsening effect.

本実施例におけるダスト搬送域4は、前記送排
風機構9および過集塵域10とに各々連通する
循環通路22の各端部に連設されている。
The dust transport area 4 in this embodiment is connected to each end of a circulation passage 22 that communicates with the ventilation mechanism 9 and the excessive dust collection area 10, respectively.

また、該ダスト搬送域4は、付着ダストの除去
時のみ搬送気流を供給し、集塵操作時はその供給
を遮断することからダンパーから成る開閉機構2
3a,23bを備えている。
Further, since the dust conveying area 4 supplies a conveying air flow only when removing attached dust and cuts off the supply during dust collection operation, an opening/closing mechanism 2 consisting of a damper is provided.
3a and 23b.

本発明における付着ダストの除去操作は、前述
の通り、ダスト含有気体の清浄化処理を中断した
状態下で行うことから、前記開閉機構7a,7
b,23a,23b、乾式ダスト払い落し機構
8、送排風機構9、過集塵域10、高電圧発生
装置12等の作動は全て自動制御される。
As described above, the operation for removing adhered dust in the present invention is performed while the cleaning process for the dust-containing gas is interrupted.
b, 23a, 23b, dry dust removal mechanism 8, ventilation mechanism 9, excessive dust collection area 10, high voltage generator 12, etc., are all automatically controlled.

通常、該自動制御は、集塵域3内のダストの付
着状態を監視するか、或いは集塵時間を予め設定
するかして、制御信号を発生させることによつて
行う。
Usually, the automatic control is performed by monitoring the state of dust adhesion within the dust collection area 3 or by setting a dust collection time in advance and generating a control signal.

なお、該制御手段は、すでに一般の電気集塵装
置で採用されており、その選択にさいしては何等
上記手段に限定されるものでなく、他の公知手段
も自由に採用し得る。
Note that the control means has already been adopted in general electrostatic precipitators, and the selection thereof is not limited to the above-mentioned means, and other known means may also be freely adopted.

また、本発明における付着ダストの除去および
その分離回収操作は搬送気流に用いたことにより
著しく短縮することができるが、ダスト含有気体
の清浄化処理を一時的に中断した状態下で行うた
めに、通常第2図に示すように少なくとも二基以
上並設され選択操作される。
Additionally, the removal of adhering dust and its separation and recovery operations in the present invention can be significantly shortened by using the conveying air stream, but since the cleaning process of the dust-containing gas is temporarily interrupted, Usually, as shown in FIG. 2, at least two or more are arranged in parallel and selectively operated.

無論、この種の装置を複数個設置する場合に
は、単なる並設以外に積重ねることも、また場合
によつては幾段にも積重ねかつそれを幾列にも並
設することもでき、その選択は自由で制限されな
い。
Of course, when a plurality of devices of this kind are installed, they can be stacked in addition to being simply installed side by side, or in some cases, they can be stacked in multiple tiers and arranged in multiple rows. The choice is free and unrestricted.

しかして、前記付着ダストの除去操作が終了す
ると、集塵通路3へのダスト含有気体の供給が再
開され、ダスト含有気体の清浄化処理が正常に行
われる。
When the operation for removing the attached dust is completed, the supply of the dust-containing gas to the dust collecting passage 3 is restarted, and the cleaning process of the dust-containing gas is normally performed.

前記第2図は、ダスト含有気体導入通路13の
横断方向に、二基の装置ユニツトが並設され、か
つその内の一基でダスト含有気体の清浄化処理が
行われ、他の一基でその間の付着ダストの除去が
行われている運転状態を示すものである。
In FIG. 2, two equipment units are installed in parallel in the transverse direction of the dust-containing gas introduction passage 13, one of which performs the cleaning process of the dust-containing gas, and the other unit performs the cleaning process of the dust-containing gas. This shows an operating state in which adhering dust is being removed during that time.

したがつて、ダスト含有気体の清浄化処理が行
われている方は、扉21がシリンダー20によつ
て開放されており、また付着ダストの除去処理が
行われている他方は、扉21が前記同様にシリン
ダー20によつて閉塞されている。
Therefore, in the case where the cleaning process of dust-containing gas is being performed, the door 21 is opened by the cylinder 20, and in the case where the process of removing attached dust is being performed, the door 21 is opened by the cylinder 20. It is likewise closed by a cylinder 20.

なお、本発明においては、第2図の如く集塵域
3が複数個備えられているものであつても、前記
送排風機構9および過集塵域10は、その操作
が選択的に行われることから一基で兼用できる。
In the present invention, even if a plurality of dust collection areas 3 are provided as shown in FIG. 2, the operation of the ventilation mechanism 9 and the excessive dust collection area 10 can be performed selectively. One unit can be used for both purposes.

また、これ等送排風機構9および過集塵域1
0の規模は、その処理風量が乾式ダスト払い落し
機構8からの噴射気体流量と、払い落しダストの
再飛散を防止し、かつ効果的に払い落しダストを
過集塵域10に導くための比較的少ない風量の
搬送気体流量だけであるので、著しく小型化され
たもので良い。
In addition, these ventilation mechanism 9 and excessive dust collection area 1
The scale of 0 is a comparison between the processing air volume and the jet gas flow rate from the dry dust removal mechanism 8 to prevent the removed dust from being scattered again and to effectively guide the removed dust to the over-collection area 10. Since the flow rate of the carrier gas is only a small amount, it is possible to use a device that is significantly smaller.

また更に、第2図の実施態様において、高電圧
発生装置12からの高電圧供給、圧搾空気供給源
14からの圧搾空気流の供給、ダスト搬送域4へ
の搬送気流の循環供給は、選択切換機24,2
5,26を介して各々行われる。
Furthermore, in the embodiment of FIG. 2, the high voltage supply from the high voltage generator 12, the supply of the compressed air flow from the compressed air supply source 14, and the circulating supply of the carrier air flow to the dust transport area 4 can be selectively switched. machine 24,2
5 and 26, respectively.

第3図は、第1図乃至第2図に示したダスト払
い落し機構8の噴射ノズル16を回転させると共
に左右に往復させるための構造を示す。
FIG. 3 shows a structure for rotating the injection nozzle 16 of the dust removal mechanism 8 shown in FIGS. 1 and 2 and reciprocating it left and right.

第3図において、27は噴射ノズル16を約90
゜回転させるために設けられるシリンダーであつ
て、該シリンダー27のピストンロツド28の先
端は、前記噴射ノズル16を備えたパイプ17が
一体的に挿入されて成るフランジ付ブツシユ29
の支持具30に止ピン31を介して回動自在に支
持される。また該シリンダー27の本体は、集塵
域3を収容するための室の側壁32に固設される
ブラケツト33に保持具34を介して保持され
る。
In FIG. 3, 27 indicates the injection nozzle 16 approximately 90
The piston rod 28 of the cylinder 27 is a cylinder provided for rotation, and the tip thereof is a flanged bush 29 into which the pipe 17 equipped with the injection nozzle 16 is integrally inserted.
It is rotatably supported by a support 30 via a stop pin 31. Further, the main body of the cylinder 27 is held via a holder 34 by a bracket 33 that is fixed to a side wall 32 of a chamber for accommodating the dust collection area 3.

なお、前記フランジ付ブツシユ29は、側壁3
2に対して回転自在に保持されている。
Note that the flanged bushing 29 is attached to the side wall 3.
It is rotatably held relative to 2.

しかして、シリンダー27のピストンロツド2
8が伸縮すると、該伸縮による往復運動は、前記
支持具30により回転運動に変えられ、該支持具
30を介して前記フランジ付ブツシユ29を回動
させる。
Therefore, piston rod 2 of cylinder 27
When 8 expands and contracts, the reciprocating movement caused by the expansion and contraction is converted into rotational movement by the support 30, and the flanged bush 29 is rotated via the support 30.

本実施例においては、噴射ノズル16を複数個
備えたパイプ17が、前記フランジ付ブツシユ2
9と一体的に回転するように、該フランジ付ブツ
シユ29内部にキー35を介して挿入され、これ
によつて、前記パイプ17はフランジ付ブツシユ
29と一体的に回動するようになつている。
In this embodiment, a pipe 17 provided with a plurality of injection nozzles 16 connects to the flanged bush 2.
The pipe 17 is inserted into the flanged bushing 29 via a key 35 so as to rotate together with the flanged bushing 29, and thereby the pipe 17 rotates integrally with the flanged bushing 29. .

36は前記噴射ノズル16を左右方向に往復さ
せるためのシリンダーであつて、該シリンダー3
6のピストンロツド37の先端は支持具38を介
してパイプ17に、またシリンダー36の本体は
フランジ付ブツシユ29に支持具39を介して
各々一体的に固設されている。
36 is a cylinder for reciprocating the injection nozzle 16 in the left and right direction;
The tip of the piston rod 37 of No. 6 is integrally fixed to the pipe 17 via a support 38, and the main body of the cylinder 36 is integrally fixed to the flanged bush 29 via the support 39.

しかして、シリンダー36のピストンロツド3
7が伸縮すると、該伸縮運動が直接パイプ17に
伝達され、これによつてパイプ17が強制的に左
右に移動する。
Therefore, the piston rod 3 of the cylinder 36
When 7 expands and contracts, the expansion and contraction movement is directly transmitted to the pipe 17, thereby forcibly moving the pipe 17 from side to side.

本実施例においては、前記フランジ付ブツシユ
29の装着側端部に位置するパイプ17の外面に
ダストが付着すると、パイプ17の往復運動に支
障を期たすので、これを防止するために蛇腹管4
0が該部を覆うように装着されている。また、こ
の種の蛇腹管40は、前記各シリンダー20,2
7,36にも装着できる。
In this embodiment, if dust adheres to the outer surface of the pipe 17 located at the mounting end of the flanged bush 29, it will hinder the reciprocating movement of the pipe 17. 4
0 is attached so as to cover this part. Further, this type of bellows tube 40 has the above-mentioned cylinders 20, 2.
It can also be installed on 7 and 36.

以上の構成を採用した本発明によれば、自動車
用トンネル内で形成されるダスト含有気体を先ず
電界が構成された集塵域3を通過させることによ
り被処理気体中からダストを集塵電極1上に捕集
してトンネル内を清浄化し、また、経時と共に前
記集塵電極1および対極に付着するダストを粗大
粒子の形でしかも前記集塵電極1から乾いた状態
でダスト搬送域4に払い落し、該ダスト搬送域4
内に払い落された粗大粒子を被処理気体よりも濃
厚な濃度で含有する分散物とし、且つ該分散物を
過集塵域10に導いて搬送気流中から分離した
ことから、処理風量が著しく大きいトンネル内の
清浄化が効果的に、しかも小型化された装置で行
え、また付着ダストの除去操作を著しく円滑でか
つ処理時間も短縮することができた。
According to the present invention employing the above configuration, dust-containing gas formed in an automobile tunnel is first passed through the dust collection area 3 in which an electric field is formed, thereby removing dust from the gas to be treated by the dust collection electrode 1. In addition, the dust that adheres to the dust collection electrode 1 and the counter electrode over time is collected in the form of coarse particles, and is also swept away from the dust collection electrode 1 in a dry state to the dust transport area 4. drop, the dust transport area 4
Since the coarse particles swept away by the dust are made into a dispersion containing a concentration higher than that of the gas to be treated, and the dispersion is led to the excessive dust collection area 10 and separated from the conveying airflow, the processing air volume is significantly increased. The inside of a large tunnel can be effectively cleaned using a compact device, and the operation for removing adhering dust can be extremely smooth and the processing time can be shortened.

また、装置ユニツトを多段に積重してもデツド
スペースが殆んど生じなかつた。
Further, even if the device units were stacked in multiple stages, almost no dead space was created.

更に、装置を長時間運転した場合にも粉塵の排
出不良というトラブルは全く生じなかつた。
Furthermore, even when the device was operated for a long time, there was no problem of insufficient dust discharge.

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

第1図は、本発明の一実施例を説明するための
一部系統的説明図であり、第2図は、第1図の具
体的説明図であり、第3図は、本発明における乾
式ダスト払い落し機構の好ましい具体例を説明す
るための斜視図であつて、 引照数字1は集塵電極、2は対極、3は集塵
域、4はダスト搬送域、7a,7bは開閉機構、
8は乾式ダスト払い落し機構、9は送排風機構、
10は過集塵域、12は高電圧発生装置、14
は圧搾空気供給源、16は噴射ノズル、20,2
7,36はシリンダーを夫々示す。
FIG. 1 is a partial systematic explanatory diagram for explaining one embodiment of the present invention, FIG. 2 is a concrete explanatory diagram of FIG. 1, and FIG. 3 is a dry type according to the present invention. It is a perspective view for explaining a preferred specific example of the dust removal mechanism, in which reference numeral 1 is a dust collection electrode, 2 is a counter electrode, 3 is a dust collection area, 4 is a dust transport area, 7a and 7b are opening/closing mechanisms,
8 is a dry dust removal mechanism, 9 is a ventilation mechanism,
10 is an excessive dust collection area, 12 is a high voltage generator, 14
is a compressed air supply source, 16 is an injection nozzle, 20,2
7 and 36 indicate cylinders, respectively.

Claims (1)

【特許請求の範囲】 1 集塵電極及び対極を備えた電気集塵域、集塵
域の下方に位置し且つこれと直接連通するダスト
搬送域、集塵域の入口及び出口を集塵操作時に開
き且つこれらをダスト搬送時に閉塞するための開
閉機構、集塵電極上の付着ダストをダスト搬送域
に払い落すための乾式ダスト払い落し機構、前記
ダスト搬送域に搬送電流を供給し且つダストを分
散物の形でダスト搬送域外に排出乃至吸引するた
めの送排風機構、及び前記送排風機構の排出乃至
吸引側に設けられた機械的集塵域から成る電気集
塵装置において、 前記乾式ダスト払い落し機構は、集塵電極面へ
付着ダスト払い落し用の圧搾空気を噴射する噴射
ノズルと、該噴射ノズルを左右に平行移動させし
かも上下に首振り運動させる機構を備えており、 且つ前記ダスト搬送域は、前記電気集塵域と実
質的に同一に設置面積を有しており、且つダスト
排出時には該ダスト搬送域の全域に亘つて層状で
一定方向のダスト搬送気流が形成されるようにな
されており、圧搾空気の吹付けにより払い落され
るダストがダスト搬送域のダスト搬送気流に乗せ
られて機械的集塵域に排出されるように関連され
ていることを特徴とする電気集塵装置。
[Scope of Claims] 1. An electric dust collection area equipped with a dust collection electrode and a counter electrode, a dust transport area located below the dust collection area and directly communicating with the dust collection area, and an inlet and an outlet of the dust collection area during dust collection operation. An opening/closing mechanism for opening and closing these during dust transport, a dry dust removal mechanism for brushing off the dust adhering to the dust collecting electrode into the dust transport area, and supplying a transport current to the dust transport area and dispersing the dust. In an electrostatic precipitator comprising a ventilation mechanism for discharging or suctioning dust in the form of objects out of a transport area, and a mechanical dust collection area provided on the discharge or suction side of the ventilation mechanism, the dry dust The blowing off mechanism is equipped with an injection nozzle that injects compressed air for blowing off the dust adhering to the dust collection electrode surface, and a mechanism that moves the injection nozzle in parallel from side to side and oscillates up and down. The conveying area has substantially the same installation area as the electrostatic precipitating area, and is configured such that a layered dust conveying airflow in a constant direction is formed over the entire area of the dust conveying area during dust discharge. Electrostatic precipitator, characterized in that the dust that is blown away by the blowing of compressed air is carried by the dust conveying airflow of the dust conveying zone and discharged to the mechanical dust collecting zone. Device.
JP9753177A 1977-08-16 1977-08-16 Method of and apparatus for electrically collecting dust Granted JPS5431677A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9753177A JPS5431677A (en) 1977-08-16 1977-08-16 Method of and apparatus for electrically collecting dust

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9753177A JPS5431677A (en) 1977-08-16 1977-08-16 Method of and apparatus for electrically collecting dust

Publications (2)

Publication Number Publication Date
JPS5431677A JPS5431677A (en) 1979-03-08
JPS6133626B2 true JPS6133626B2 (en) 1986-08-02

Family

ID=14194826

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9753177A Granted JPS5431677A (en) 1977-08-16 1977-08-16 Method of and apparatus for electrically collecting dust

Country Status (1)

Country Link
JP (1) JPS5431677A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61107962A (en) * 1984-10-30 1986-05-26 Matsushita Seiko Co Ltd Electric dust precipitator
JPS63152649U (en) * 1987-03-30 1988-10-06
JP2607680B2 (en) * 1989-05-09 1997-05-07 三菱重工業株式会社 Electric precipitator and operating method thereof
KR20170020682A (en) * 2015-08-14 2017-02-23 (주)와이에이치비 filter washing apparatus for electric dust collector

Also Published As

Publication number Publication date
JPS5431677A (en) 1979-03-08

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