JPH06238120A - Method and device for cleaning contaminated air - Google Patents

Method and device for cleaning contaminated air

Info

Publication number
JPH06238120A
JPH06238120A JP5028304A JP2830493A JPH06238120A JP H06238120 A JPH06238120 A JP H06238120A JP 5028304 A JP5028304 A JP 5028304A JP 2830493 A JP2830493 A JP 2830493A JP H06238120 A JPH06238120 A JP H06238120A
Authority
JP
Japan
Prior art keywords
water
air
chamber
contaminated
purification
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.)
Granted
Application number
JP5028304A
Other languages
Japanese (ja)
Other versions
JPH0753223B2 (en
Inventor
Kaoru Umeya
薫 梅屋
Masami Suzuki
正身 鈴木
Masaharu Iwamiya
正治 岩宮
Junji Morishige
順次 森重
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.)
Toyo Netsu Kogyo Kaisha Ltd
Original Assignee
Toyo Netsu Kogyo Kaisha 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 Toyo Netsu Kogyo Kaisha Ltd filed Critical Toyo Netsu Kogyo Kaisha Ltd
Priority to JP5028304A priority Critical patent/JPH0753223B2/en
Publication of JPH06238120A publication Critical patent/JPH06238120A/en
Publication of JPH0753223B2 publication Critical patent/JPH0753223B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Central Air Conditioning (AREA)
  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)
  • Drying Of Gases (AREA)

Abstract

PURPOSE:To provide a method and device for cleaning contaminated air where contaminants are effectively and surely removed to maintain person's health in the poor environment, such as a tollbooth for a toll highway. CONSTITUTION:Cleaning water is introduced under conditions of pressurization into a cleaning chamber 15 to spray it into the chamber from a nozzle 5. Contaminated air is introduced under conditions of pressurization or vacuum suction into the chamber to bring it into contact with the water particles 6 thus sprayed, causing contaminants to be absorbed onto the water particles side. The cleaned air is blown to a place to be given air conditioning from the chamber and also the water particles absorbing the contaminants are collected to discharge them from the chamber as contaminated water.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、汚染空気浄化方法およ
び装置に関し、特に有料道路の料金徴収ブースの空調処
理に適した汚染空気浄化方法および装置に関するもので
ある。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a polluted air purification method and device, and more particularly to a polluted air purification method and device suitable for air conditioning of a toll road toll collection booth.

【0002】[0002]

【従来の技術】高速自動車道路等の自動車専用道路の料
金徴収所では、料金徴収ブース内の作業員が通行料金の
徴収や領収書の発行等を行っている。従来の有料道路の
料金徴収ブース内における空調等の環境維持は、ブース
の屋根に冷暖房機を取り付けて冷暖房についてのみ行
い、冷暖房空気を送風する場合には室内空気(ブース内
空気)を循環させて行っていた。
2. Description of the Related Art At a toll collection point on a motorway such as a highway, workers in a toll booth collect tolls and issue receipts. To maintain the environment such as air conditioning in the conventional toll collection booth on toll roads, an air conditioner is installed on the roof of the booth and only air conditioning is performed. I was going.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、最近で
は自動車の数が増加し、有料道路の料金所付近では常に
車が渋滞した状態であり、ブース周辺の空気の質は非常
に劣悪となっている。即ち、車から排出される硫黄酸化
物(SOX)や窒素酸化物(NOX)および炭素酸化物
(COX)等の有害ガス成分の濃度が非常に高くなり、
またタイヤや道路からの粉塵 等が高濃度で混入してい
る。このため、従来のようにブース内空調を室内空気の
循環のみで行い空気成分の調整を行わないと、料金徴収
ブース内で働く作業員が長時間連続して作業をした場合
に、人体生理上好ましくない影響を与え作業員の健康障
害を引き起こすおそれが大きかった。
However, recently, the number of automobiles has increased, and cars are constantly congested near toll gates on toll roads, and the quality of air around the booth is extremely poor. . That is, the concentration of harmful gas components such as sulfur oxides discharged from the vehicle (SO X) and nitrogen oxides (NO X) and carbon oxides (CO X) is very high,
In addition, dust from tires and roads is mixed in at a high concentration. For this reason, if the air conditioning inside the booth is performed only by circulating the indoor air as in the past and the air components are not adjusted, the human physiology will not be affected if the workers working inside the toll collection booth work continuously for a long time. There was a great possibility that it would have an unfavorable effect and cause health problems for workers.

【0004】一方、大気汚染対策としてのSOX、NOX
排除技術はある程度熟成されているが、COX対策は未
だ確立された技術が無く、前述のように大気汚染による
人体の健康障害を防止するために、空気中の有害成分を
効率よく除去する手段が望まれている。
On the other hand, SO X and NO X as measures against air pollution
Although the elimination technology has been matured to some extent, there is no established technology for CO X measures, and as mentioned above, a means for efficiently removing harmful components in the air in order to prevent human health damage due to air pollution. Is desired.

【0005】SOX、NOXおよびCOXの除去を有料道
路料金徴収ブースというような局地的な場所で解決する
ために採用を考慮できる手段としては次のような方法が
ある。
There are the following methods which can be considered for adoption in order to solve the removal of SO X , NO X and CO X at a local place such as a toll road collection booth.

【0006】1、気相処理技術 (1−1)気体有害成分分離膜を使用する方法 (1−2)有害成分を吸収分離する方法 2、液相処理技術 (2−1)液中で気泡化させ液に吸収させる方法 (2−2)散水による有害成分ガスを吸収させる方法。1. Gas phase treatment technology (1-1) Method of using gas harmful component separation membrane (1-2) Method of absorbing and separating harmful components 2. Liquid phase treatment technology (2-1) Bubbles in liquid (2-2) Method of absorbing harmful gas by sprinkling water.

【0007】これらの方法のうち、(1−1)は気体成
分分離膜として分子篩を必要とするので確実な方法であ
るが高価になる。(1−2)の気相状吸収分離を行えば
経済上の難点は解決可能であるが処理効率の点で劣る。
(2−1)の液中微細気泡化による母液(水道水)吸収
法は、実用上有用な方法ではあるが、吸収された有害成
分の再放出の問題がある。一方、(2−2)の散水液滴
(水道水)による吸収法によれば、散水量に対して吸収
量は微量なので、処理後の大気中への再放出の心配はな
い。
Of these methods, (1-1) is a reliable method because it requires a molecular sieve as a gas component separation membrane, but it is expensive. If the gas phase absorption and separation of (1-2) is performed, the economic difficulty can be solved, but the treatment efficiency is poor.
Although the mother liquor (tap water) absorption method (2-1) by forming fine bubbles in the liquid is a practically useful method, it has a problem of re-release of absorbed harmful components. On the other hand, according to (2-2) the absorption method using sprinkled liquid droplets (tap water), since the absorbed amount is small relative to the sprinkled amount, there is no concern about re-release into the atmosphere after treatment.

【0008】本発明は上記従来技術の各点に鑑みなされ
たものであって、有料道路の料金徴収ブース等の劣悪な
環境化で効率よく確実に汚染物質を除去して人体の健康
を守ことができる汚染空気浄化方法および装置の提供を
目的とする。
The present invention has been made in view of the above-mentioned respective points of the prior art, and in order to protect human health by efficiently and reliably removing pollutants in a bad environment such as a toll road toll collection booth. It is an object of the present invention to provide a method and a device for purifying contaminated air.

【0009】[0009]

【課題を解決するための手段】前記目的を達成するた
め、本発明に係る汚染空気浄化方法においては、浄化チ
ャンバー内に浄化用の水を加圧状態で導入し、この水を
ノズルより前記チャンバー内に噴霧し、汚染空気を該チ
ャンバー内に加圧あるいは減圧吸入状態で導入して前記
噴霧された水滴粒子と接触させることにより汚染物質を
水滴粒子側に吸収させ、清浄化された空気を前記チャン
バーから空調すべき場所に導入して吹き出すとともに前
記汚染物質を吸収した水滴粒子を集めて汚染水として前
記チャンバーから排出することを特徴とする。
In order to achieve the above object, in the method for purifying contaminated air according to the present invention, purifying water is introduced into the purifying chamber under pressure, and the water is introduced from the nozzle into the chamber. The pollutants are absorbed into the water droplet particles side by spraying into the chamber and introducing the polluted air into the chamber under pressure or reduced pressure inhalation state to contact with the sprayed water droplet particles, and the purified air is It is characterized in that it is introduced from the chamber to a place to be air-conditioned and blown out, and the water droplet particles absorbing the pollutant are collected and discharged from the chamber as polluted water.

【0010】好ましい実施例においては、前記空調すべ
き場所は有料道路の料金徴収ブースであり、このブース
内の湿度上昇防止用のデミスタを介して前記清浄空気を
該料金徴収ブース内に導入して吹き出している。
In a preferred embodiment, the location to be air-conditioned is a toll road toll collection booth, and the clean air is introduced into the toll collection booth via a humor in the booth to prevent a rise in humidity. It's blowing.

【0011】別の好ましい実施例においては、前記浄化
用の水として加圧状態で送水されている水道水をそのま
ま使用するかあるいはこの水道水を受水タンクに受けポ
ンプで圧送するとともに、該浄化用の水に水酸化カルシ
ウム溶液を混入させている。
In another preferred embodiment, tap water that is being sent under pressure is used as is as the water for purification, or this tap water is pumped to a receiving tank by a receiving pump and the purification is performed. Calcium hydroxide solution is mixed in water for use.

【0012】別の好ましい実施例においては、前記浄化
チャンバー内のノズルの上流側に、汚染空気導入口を設
け、該汚染空気導入口と前記ノズルとの間に除湿用ゼオ
ライトペレット層およびCOX吸着用生石灰ペレット層
を設けている。
[0012] In another preferred embodiment, a polluted air inlet is provided upstream of the nozzle in the purification chamber, and a dehumidifying zeolite pellet layer and CO X adsorption are provided between the polluted air inlet and the nozzle. A quicklime pellet layer is provided.

【0013】上記汚染空気浄化方法を実施するための空
気浄化装置は、受水タンクと、浄化チャンバーと、該受
水タンクおよび浄化チャンバーを連結する給水配管と、
該給水配管上に設けた送水ポンプと、前記浄化チャンバ
ー内の給水配管先端に設けた散水噴霧用のノズルと、汚
染空気を前記浄化チャンバー内に圧送するための送風機
と、前記浄化チャンバー内に圧送された汚染空気を前記
ノズルから散水噴霧された水滴粒子と接触した後に清浄
空気として取り出す清浄空気出口と、前記汚染空気と接
触した後の水滴粒子を集めて汚染水として前記浄化チャ
ンバーから排出するための配水管とを具備している。
An air purification apparatus for carrying out the method for purifying polluted air comprises a water receiving tank, a purification chamber, and a water supply pipe connecting the water receiving tank and the purification chamber.
A water pump provided on the water supply pipe, a nozzle for spraying water spray provided at the tip of the water supply pipe in the purification chamber, a blower for pumping contaminated air into the purification chamber, and a pressure pump into the purification chamber. The clean air outlet for taking out the polluted air that has been sprayed from the nozzle as clean air after contacting the sprayed water droplet particles, and collecting the water droplet particles after contacting the polluted air and discharging it as polluted water from the purification chamber. It has a water pipe.

【0014】[0014]

【作用】有料道路の料金徴収ブース等において、ブース
内空気の成分を調整するために、浄化チャンバー(アス
ピレータ本体)に水道水を加圧状態で導入し、この水道
水をチャンバー内で先端径を絞ったノズルより吹き出し
て逆円弧状に噴霧散水する。ノズル付近に設けた空気流
入口よりブース内の汚染空気を前記チャンバー内に加圧
状態あるいはノズルの負圧作用による減圧吸入状態で導
入する。これにより、汚染空気はノズルから発生した微
細水滴と十分接触し、汚染空気中に含まれる汚染ガス、
汚染微粒子、有害微生物等が水滴側に吸収される。汚染
物質を吸収除去され清浄化された空気はブース内に導入
され吹き出される。汚染物質を吸収した水滴はチャンバ
ー下部に集められ汚染水として外部に排出される。
[Operation] In a toll road toll collection booth, etc., tap water is introduced under pressure into the purification chamber (aspirator body) in order to adjust the components of the air in the booth, and this tap water is adjusted to the tip diameter in the chamber. It is sprayed from a narrowed nozzle and sprayed in a reverse arc shape. The polluted air in the booth is introduced into the chamber from an air inlet provided near the nozzle in a pressurized state or a reduced pressure suction state by the negative pressure action of the nozzle. As a result, the contaminated air is in sufficient contact with the fine water droplets generated from the nozzle, and the contaminated gas contained in the contaminated air,
Contaminant particles, harmful microorganisms, etc. are absorbed on the water drop side. The air that has been cleaned by absorbing and removing pollutants is introduced into the booth and blown out. Water droplets that have absorbed the pollutants are collected in the lower part of the chamber and discharged to the outside as polluted water.

【0015】[0015]

【実施例】図1は本発明の実施例に係るアスピレータ方
式の汚染空気浄化装置の一例の概略構成図である。1は
市水配管、2は受水タンク、3は給水配管、4は送水ポ
ンプ、5は噴霧ノズル、6は噴霧水、7は送風機、8は
汚染空気入口管、9は清浄空気出口管、10は配水管、
15はアスピレータ本体を構成する浄化チャンバーであ
る。市水配管1は受水タンク2に連結される。受水タン
ク2と浄化チャンバー15は給水配管3で連結され、給
水配管3上に送水ポンプ4が設けられる。給水配管3の
先端には径を絞ったノズル5が取り付けられる。ノズル
5は、浄化チャンバー15内の上部に配置される。汚染
空気入口管8はこのノズル5の近傍位置に設けられる。
清浄空気出口管9は浄化チャンバー15の下部に設けら
れる。配水管10は浄化チャンバー15の底部に連結さ
れる。
FIG. 1 is a schematic configuration diagram of an example of an aspirator-type contaminated air purifying apparatus according to an embodiment of the present invention. 1 is a city water pipe, 2 is a water receiving tank, 3 is a water supply pipe, 4 is a water supply pump, 5 is a spray nozzle, 6 is spray water, 7 is a blower, 8 is a contaminated air inlet pipe, 9 is a clean air outlet pipe, 10 is a water pipe,
Reference numeral 15 is a purification chamber that constitutes the main body of the aspirator. The city water pipe 1 is connected to the water receiving tank 2. The water receiving tank 2 and the purification chamber 15 are connected by a water supply pipe 3, and a water supply pump 4 is provided on the water supply pipe 3. A nozzle 5 having a reduced diameter is attached to the tip of the water supply pipe 3. The nozzle 5 is arranged in the upper part of the purification chamber 15. The contaminated air inlet pipe 8 is provided near the nozzle 5.
The clean air outlet pipe 9 is provided in the lower portion of the purification chamber 15. The water pipe 10 is connected to the bottom of the purification chamber 15.

【0016】市水配管1より受水タンク2に市水(水道
水)を受ける(矢印A)。受水タンク2に溜められた水
道水は送水ポンプ4により給水配管3を介して矢印Bの
ようにアスピレータ(浄化チャンバー15)に圧送され
る。浄化チャンバー15内に圧送された水道水はノズル
5により上部から下方に向けて円弧状または逆円弧状に
拡散噴霧され、噴霧水6となって浄化チャンバー15内
全体に微細水滴粒子として拡散し落下する。
City water (tap water) is received from the city water pipe 1 into the water receiving tank 2 (arrow A). The tap water stored in the water receiving tank 2 is pressure-fed by the water feed pump 4 to the aspirator (purification chamber 15) through the water supply pipe 3 as shown by an arrow B. The tap water pumped into the purification chamber 15 is diffused and sprayed from the upper part to the lower part by the nozzle 5 in an arc shape or an inverse arc shape, and becomes sprayed water 6 that is diffused as fine water droplet particles into the entire purification chamber 15 and falls. To do.

【0017】なお、水道水を一旦受水タンク2に溜めて
これをポンブ4で圧送する上記構成に代えて、加圧状態
の市水配管からの水道水を適当な制御弁等を介して直接
浄化チャンバー15内に導入してもよい。
Instead of the above-described structure in which tap water is temporarily stored in the water receiving tank 2 and is pumped by the pump 4, tap water from the pressurized city water pipe is directly supplied through an appropriate control valve or the like. It may be introduced into the purification chamber 15.

【0018】一方、空調すべき部屋、例えば有料道路の
料金徴収ブース内の汚染空気は、送風機7で矢印Cのよ
うに汚染空気入口管8を通して浄化チャンバー15内の
上部ノズル5の近傍に圧送される。この汚染空気は、自
動車の排気ガス成分であるNOXやCOXまた場合によっ
てはSOXなどの有害ガス成分や煤その他の塵埃等の汚
染物質や有害微生物等を含んでいる。このような汚染物
質等は、汚染空気が浄化チャンバー15内で噴霧水6と
十分接触することにより、水滴粒子側に吸収され汚染空
気が浄化される。汚染物質等が除去された空気は、浄化
チャンバー下部の清浄空気出口管9を通して矢印Dのよ
うに料金徴収ブース内に導入され清浄空気として吹き出
される。
On the other hand, the contaminated air in the toll collection booth of the room to be air-conditioned, for example, a toll road, is blown by the blower 7 through the contaminated air inlet pipe 8 to the vicinity of the upper nozzle 5 in the purification chamber 15 as indicated by arrow C. It The contaminated air, when also NO X and CO X by contains contaminants and harmful microorganisms, such as harmful gas components and soot other dust, such as SO X is an exhaust gas component of a motor vehicle. Such pollutants and the like are absorbed on the side of the water droplets to purify the contaminated air when the contaminated air sufficiently contacts the spray water 6 in the purifying chamber 15. The air from which pollutants and the like have been removed is introduced into the charge collection booth as shown by arrow D through the clean air outlet pipe 9 in the lower part of the purification chamber and blown out as clean air.

【0019】なお、浄化チャンバー15内に汚染空気を
加圧状態で導入するための送風機7を省略して、チャン
バー15内に発生する負圧により汚染空気を自然吸引す
ることもできる。即ち、アスピレータ(浄化チャンバー
15)内のノズル5から散水された噴霧水6の上側空間
部は、噴霧水の流速作用により負圧状態となるため、送
風機を用いて汚染空気をアスピレータ内に圧送しなくて
もアスピレータ内に発生する負圧により吸引されるから
である。送風機を用いれば汚染空気の導入が確実に効率
よく行われる。
The blower 7 for introducing the polluted air into the purification chamber 15 under pressure may be omitted, and the polluted air may be naturally sucked by the negative pressure generated in the chamber 15. That is, the upper space portion of the spray water 6 sprayed from the nozzle 5 in the aspirator (cleaning chamber 15) is in a negative pressure state due to the flow velocity effect of the spray water, and therefore the contaminated air is pressure-fed into the aspirator using a blower. This is because the negative pressure generated in the aspirator sucks the gas even if it is not used. If a blower is used, the introduction of polluted air can be reliably and efficiently performed.

【0020】一方、有害ガス成分等の汚染物質を吸収し
た水滴粒子は浄化チャンバー15の底部に集められ、配
水管10を通して矢印Eのようにアスピレータ外部に排
出される。
On the other hand, water droplet particles that have absorbed pollutants such as harmful gas components are collected at the bottom of the purification chamber 15 and discharged to the outside of the aspirator through the water distribution pipe 10 as indicated by arrow E.

【0021】ここで噴霧水6と汚染空気の接触による汚
染物質の吸収作用を増進させるためには、噴霧水の水滴
粒子は微粒子である程よい。しかしながら、水滴粒子を
微細化する程、この水滴微粒子が清浄空気といっしょに
浄化チャンバー15から運び出され(キャリアウト現
象)、料金徴収ブース内に吹き出されてブース内の湿度
を上昇させる。このようなキャリアウトによるブース内
の湿度上昇を防止するために、清浄空気出口管9の入口
側にデミスタ(図示しない)を設けてキャリアウト量を
減少させることが望ましい。
Here, in order to enhance the action of absorbing the pollutants by the contact between the spray water 6 and the polluted air, it is preferable that the water droplet particles of the spray water are fine particles. However, as the water droplet particles become finer, the water droplet particles are carried out from the purification chamber 15 together with the clean air (carrier out phenomenon) and blown out into the toll collection booth to increase the humidity in the booth. In order to prevent such a rise in humidity in the booth due to carrier-out, it is desirable to provide a demister (not shown) on the inlet side of the clean air outlet pipe 9 to reduce the amount of carrier-out.

【0022】上記構成の汚染空気浄化装置に対しさらに
汚染ガス分離促進手段を付加してもよい。この汚染ガス
分離促進手段としては、例えば受水タンク2に取り付け
た水酸化カルシウム液滴下混入装置(図示しない)が用
いられ、受水タンク内の水に水酸化カルシウム(Ca
(OH)2)の溶液を微量づつ滴下混入する。これによ
り、浄化チャンバー15内で散水される噴霧水が水酸化
カルシウム溶液となり、この噴霧水がブースから導入さ
れた汚染空気中の有害ガス成分を吸収してカルシウム塩
を作り沈殿するため、有害ガスの分離吸収が促進され
る。
A polluted gas separation promoting means may be added to the polluted air purifying apparatus having the above structure. As the polluted gas separation promoting means, for example, a calcium hydroxide droplet under-mixing device (not shown) attached to the water receiving tank 2 is used, and calcium hydroxide (Ca) is added to the water in the water receiving tank.
A small amount of (OH) 2 ) solution is mixed in. As a result, the sprayed water sprinkled in the purification chamber 15 becomes a calcium hydroxide solution, and this sprayed water absorbs harmful gas components in the contaminated air introduced from the booth to form calcium salts and precipitates. The separation and absorption of is promoted.

【0023】図2は、本発明の別の実施例に係る汚染空
気浄化装置の要部構成図である。図1の実施例と同一ま
たは対応する部材には同じ番号を付してある。この実施
例は、アスピレータの上部に除湿用のゼオライトペレッ
ト槽11およびその下側に炭素酸化物除去用の生石灰ペ
レット槽12を設けた構成である。汚染空気入口管8は
ゼオライトペレット槽11の上流側に開口する。生石灰
ペレット槽12の下側には、アスピレータを構成する浄
化チャンバー内での空気流を均一にするためのディスト
リビュータ13が設けられる。14は仕切り網である。
FIG. 2 is a schematic view of a main part of a polluted air purifying apparatus according to another embodiment of the present invention. The same or corresponding members as those in the embodiment of FIG. 1 are designated by the same reference numerals. In this embodiment, a zeolite pellet tank 11 for dehumidification is provided above the aspirator, and a quick lime pellet tank 12 for removing carbon oxide is provided below the zeolite pellet tank 11. The contaminated air inlet pipe 8 opens on the upstream side of the zeolite pellet tank 11. Below the quicklime pellet tank 12, a distributor 13 is provided for uniformizing the air flow in the purification chamber that constitutes the aspirator. 14 is a partition net.

【0024】料金徴収ブースからの汚染空気は送風機7
によりアスピレータの頂部から圧送され、ゼオライトペ
レット層11および生石灰ペレット層12を通過してデ
ィストリビュータ13で均質に分散され浄化チャンバー
内を上から下に流れる。ここで、汚染空気がゼオライト
ペレット層11を通過することにより水分が吸収されて
除去される。この乾燥空気が生石灰ペレット層12を通
過することにより、COxが除去される。この場合、生
石灰ペレットは空気中の水分によりCOXの吸収機能が
急速に低下するため、この生石灰ペレット層12の上流
側に除湿用のゼオライトペレット層11を設けておくこ
とが望ましい。
The contaminated air from the charge collection booth is blower 7
Is sent by pressure from the top of the aspirator, passes through the zeolite pellet layer 11 and the quicklime pellet layer 12, is uniformly dispersed by the distributor 13, and flows in the purification chamber from top to bottom. Here, the contaminated air passes through the zeolite pellet layer 11 to absorb and remove water. By passing this dry air through the quicklime pellet layer 12, CO x is removed. In this case, quick lime pellets have a rapidly reduced CO X absorption function due to moisture in the air, so it is desirable to provide a dehumidifying zeolite pellet layer 11 on the upstream side of the quick lime pellet layer 12.

【0025】このようにして水分およびCOX成分を除
去された空気は、図1の実施例の場合と同様に、ノズル
5からの噴霧水6に接触して残りのNOXおよびSOX
効果的に水滴粒子に吸収され除去される。このような構
成により、排気ガス中の有害成分であるCOX、NOX
SOXが効率よく完全に除去される。その他の構成およ
び作用効果については前記図1の実施例と同様である。
The air from which the water and CO X components have been removed in this way comes into contact with the spray water 6 from the nozzle 5 and the remaining NO X and SO X are effective, as in the case of the embodiment of FIG. Water particles are absorbed and removed. With such a configuration, CO X , NO X , which are harmful components in the exhaust gas,
SO X is efficiently and completely removed. Other configurations and operational effects are similar to those of the embodiment shown in FIG.

【0026】前述の図1の実施例によれば、ブース内の
汚染空気から、NOXに関しては99%程度、SOXに関
しては98.5%、COXに関しては95%程度の除去
が可能である。また図2の実施例によれば、特にCOX
の除去率が改善され、浄化装置出口部で98%程度の除
去が達成できる。
According to the above-described embodiment shown in FIG. 1, about 99% of NO x , about 98.5% of SO x and about 95% of CO x can be removed from the contaminated air in the booth. is there. According to the embodiment of FIG. 2, in particular CO X
The removal rate is improved, and removal of about 98% can be achieved at the outlet of the purifier.

【0027】[0027]

【発明の効果】以上説明したように、本発明に係る汚染
空気浄化方法においては、アスピレータ式の浄化チャン
バー内で水滴粒子を噴霧しこの水滴粒子に汚染空気を十
分接触させることにより空気中の汚染物質を水滴粒子側
に吸収させて汚染空気を浄化し、汚染物質を吸収した水
滴粒子を集めてチャンバー外へ排出しているため、汚染
物質の除去が確実に行われ、特に有料道路の料金徴収ブ
ースの空調システムに適用すれば、排気ガス中の有害成
分が有効に除去されブース内で働く作業員の健康が守ら
れる。
As described above, in the method for purifying contaminated air according to the present invention, water particles are sprayed in the aspirator type purifying chamber and the contaminated air is sufficiently brought into contact with the water particles to contaminate the air. The substances are absorbed by the water droplets to purify the contaminated air, and the water droplets that have absorbed the contaminants are collected and discharged to the outside of the chamber, so the contaminants are reliably removed, especially toll collection on toll roads. When applied to a booth air conditioning system, harmful components in exhaust gas are effectively removed and the health of workers working in the booth is protected.

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

【図1】 本発明の実施例に係るアスピレータ式の汚染
空気浄化装置の構成説明図である。
FIG. 1 is a configuration explanatory view of an aspirator-type contaminated air purifying apparatus according to an embodiment of the present invention.

【図2】 本発明の別の実施例に係るアスピレータ式の
汚染空気浄化装置の要部構成説明図である。
FIG. 2 is an explanatory diagram of a main part configuration of an aspirator-type contaminated air purifying apparatus according to another embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1…市水配管 2…受水
タンク 3…給水配管 4…送水
ポンプ 5…ノズル 6…噴霧
水 7…送風機 8…汚染
空気入口管 9…清浄空気出口管 10…排
水管 11…ゼオライトペレット層 12…生
石灰ペレット層 13…ディストリビュータ 14…仕
切り網 15…浄化チャンバー
1 ... City water pipe 2 ... Water receiving tank 3 ... Water supply pipe 4 ... Water pump 5 ... Nozzle 6 ... Spray water 7 ... Blower 8 ... Contamination air inlet pipe 9 ... Clean air outlet pipe 10 ... Drain pipe 11 ... Zeolite pellet layer 12 ... quicklime pellet layer 13 ... distributor 14 ... partition net 15 ... purification chamber

─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成5年6月22日[Submission date] June 22, 1993

【手続補正1】[Procedure Amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】特許請求の範囲[Name of item to be amended] Claims

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【特許請求の範囲】[Claims]

───────────────────────────────────────────────────── フロントページの続き (72)発明者 鈴木 正身 東京都中央区京橋二丁目5番12号 東洋熱 工業株式会社内 (72)発明者 岩宮 正治 東京都中央区京橋二丁目5番12号 東洋熱 工業株式会社内 (72)発明者 森重 順次 東京都中央区築地四丁目1番1号 ウルテ ック株式会社内 ─────────────────────────────────────────────────── ─── Continuation of front page (72) Masami Suzuki 2-5-12, Kyobashi, Chuo-ku, Tokyo Toyo Heat Industrial Co., Ltd. (72) Masaharu Iwamiya 2-5-12, Kyobashi, Chuo-ku, Tokyo Toyo Atsushi Kogyo Co., Ltd. (72) Inventor Morishige Sequentially 4-1-1 Tsukiji, Chuo-ku, Tokyo Ultec Co., Ltd.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】浄化チャンバー内に浄化用の水を加圧状態
で導入し、この水をノズルより前記チャンバー内に噴霧
し、汚染空気を該チャンバー内に導入して前記噴霧され
た水滴粒子と接触させることにより汚染物質を水滴粒子
側に吸収させ、清浄化された空気を前記チャンバーから
空調すべき場所に吹き出すとともに前記汚染物質を吸収
した水滴粒子を集めて汚染水として前記チャンバーから
排出することを特徴とする汚染空気浄化方法。
1. Purification water is introduced into a purification chamber under pressure, the water is sprayed from the nozzle into the chamber, and contaminated air is introduced into the chamber to produce the sprayed water droplet particles. The contact is made to absorb the pollutants on the side of the water droplets, the purified air is blown out from the chamber to a place to be air-conditioned, and the water droplets absorbed the pollutants are collected and discharged from the chamber as contaminated water. A method for purifying polluted air characterized by.
【請求項2】前記空調すべき場所は有料道路の料金徴収
ブースであり、前記清浄空気をブース内の湿度上昇防止
用のデミスタを介して該料金徴収ブース内に吹き出すこ
とを特徴とする請求項1に記載の汚染空気浄化方法。
2. The area to be air-conditioned is a toll road toll collection booth, and the clean air is blown into the toll collection booth through a demister for preventing humidity increase in the booth. 1. The method for purifying polluted air according to 1.
【請求項3】前記浄化用の水としては、加圧状態で送水
されている水道水をそのまま使用するかあるいは該水道
水を受水タンクに受けポンプで圧送するとともに、さら
には該浄化用の水に水酸化カルシウム溶液を混入させた
ことを特徴とする請求項1に記載の汚染空気浄化方法。
3. As the water for purification, tap water sent under pressure may be used as it is, or the tap water may be pumped to a receiving tank by a pump, and further purified. The method for purifying polluted air according to claim 1, wherein a calcium hydroxide solution is mixed with water.
【請求項4】前記浄化チャンバー内のノズルの上流側
に、汚染空気導入口を設け、該汚染空気導入口と前記ノ
ズルとの間に除湿用ゼオライトペレット層およびN
X、SOX、さらにはCOX吸着用生石灰ペレット層を
設けたことを特徴とする請求項1に記載の汚染空気浄化
方法。
4. A contaminated air inlet is provided upstream of a nozzle in the purification chamber, and a dehumidifying zeolite pellet layer and N are provided between the contaminated air inlet and the nozzle.
O X, SO X, more contaminated air purifying method according to claim 1, characterized in that a CO X attraction quicklime pellet layer.
【請求項5】受水タンクと、浄化チャンバーと、該受水
タンクおよび浄化チャンバーを連結する給水配管と、該
給水配管上に設けた送水ポンプと、前記浄化チャンバー
内の給水配管先端に設けた散水噴霧用のノズルと、汚染
空気を前記浄化チャンバー内に圧送するための送風機
と、前記浄化チャンバー内に圧送された汚染空気を前記
ノズルから散水噴霧された水滴粒子と接触した後に清浄
空気として取り出す清浄空気出口と、前記汚染空気と接
触した後の水滴粒子を集めて汚染水として前記浄化チャ
ンバーから排出するための配水管とを具備したことを特
徴とする汚染空気浄化装置。
5. A water receiving tank, a purification chamber, a water supply pipe connecting the water receiving tank and the purification chamber, a water supply pump provided on the water supply pipe, and a water supply pipe tip in the purification chamber. Nozzle for spraying spray, blower for pumping polluted air into the purification chamber, polluted air pumped into the purification chamber is taken out as clean air after coming in contact with the sprayed water droplet particles from the nozzle A contaminated air purification apparatus comprising: a clean air outlet; and a water pipe for collecting water droplet particles after contacting the contaminated air and discharging the water as contaminated water from the purification chamber.
JP5028304A 1993-02-17 1993-02-17 Contaminated air purification method and device Expired - Fee Related JPH0753223B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5028304A JPH0753223B2 (en) 1993-02-17 1993-02-17 Contaminated air purification method and device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5028304A JPH0753223B2 (en) 1993-02-17 1993-02-17 Contaminated air purification method and device

Publications (2)

Publication Number Publication Date
JPH06238120A true JPH06238120A (en) 1994-08-30
JPH0753223B2 JPH0753223B2 (en) 1995-06-07

Family

ID=12244885

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5028304A Expired - Fee Related JPH0753223B2 (en) 1993-02-17 1993-02-17 Contaminated air purification method and device

Country Status (1)

Country Link
JP (1) JPH0753223B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011505514A (en) * 2007-11-27 2011-02-24 インブ ジャコブセン Equipment for reducing most of the carbon dioxide produced by all internal combustion engines and industrial activities
KR101430120B1 (en) * 2009-10-05 2014-08-18 가부시키가이샤 오메가 Gas purification apparatus
JP2014156837A (en) * 2013-02-18 2014-08-28 Denso Corp Engine aftertreatment device using liquid

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62254823A (en) * 1986-04-25 1987-11-06 Takeshi Morita Clarifier for polluted air

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62254823A (en) * 1986-04-25 1987-11-06 Takeshi Morita Clarifier for polluted air

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011505514A (en) * 2007-11-27 2011-02-24 インブ ジャコブセン Equipment for reducing most of the carbon dioxide produced by all internal combustion engines and industrial activities
KR101430120B1 (en) * 2009-10-05 2014-08-18 가부시키가이샤 오메가 Gas purification apparatus
JP2014156837A (en) * 2013-02-18 2014-08-28 Denso Corp Engine aftertreatment device using liquid

Also Published As

Publication number Publication date
JPH0753223B2 (en) 1995-06-07

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