JPH03186276A - Smoke extinguishing device - Google Patents

Smoke extinguishing device

Info

Publication number
JPH03186276A
JPH03186276A JP32779789A JP32779789A JPH03186276A JP H03186276 A JPH03186276 A JP H03186276A JP 32779789 A JP32779789 A JP 32779789A JP 32779789 A JP32779789 A JP 32779789A JP H03186276 A JPH03186276 A JP H03186276A
Authority
JP
Japan
Prior art keywords
smoke
spray nozzle
pressure water
water droplets
control means
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
JP32779789A
Other languages
Japanese (ja)
Inventor
Shigeo Watanabe
渡辺 茂男
Kenji Okazaki
健志 岡崎
Tsugukazu Hayashi
二一 林
Teruo Yamada
山田 輝男
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.)
Nagao Kogyo Co Ltd
Original Assignee
Nagao Kogyo 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 Nagao Kogyo Co Ltd filed Critical Nagao Kogyo Co Ltd
Priority to JP32779789A priority Critical patent/JPH03186276A/en
Publication of JPH03186276A publication Critical patent/JPH03186276A/en
Priority to US08/111,399 priority patent/US5353879A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To quickly extinguish smoke in the case the room is filled with smoke by providing a spray nozzle provided on an indoor ceiling part or a wall part, a high pressure water supply part for supplying high pressure water to which a surface active agent is added within a range of specific PPM to this nozzle, and a control means for controlling the supply of the high pressure water to the spray nozzle. CONSTITUTION:When a building passage 100 is filled with smoke, a smoke sensor 3 (control means) outputs a signal corresponding to smoke density to a discriminating part 4 (control means), and when the smoke density exceeds a prescribed level, the discriminating part 4 opens a valve device (control means), and sprays water droplets of fine particles through a spray nozzle 1 from a high pressure water supply part 2. The water droplets catch smoke particles on the way of dropping down, and extinguish smoke in the passage 100. To the water droplets, positive high potential is given, therefore, smoke particles generally electrified to negative are caught by electrostatic force. Also, since a surface active agent of 1-3000PPM is added to the water droplets, the water droplets come to easily smoke particles, and the smoke particle catching capacity of water droplets is improved remarkably.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、建物火災時に発生する煙を低減する消煙装置
に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a smoke extinguishing device for reducing smoke generated during a building fire.

[従来の技術] 最近のビル火災などにおける人的被害は、発生した煙を
その主な原因としている。すなわち、火災初期に建材な
どから発生する大量の煙によって、視界を遮られて避難
が遅れ、そのうちに煙や有毒ガス、更には火熱により致
命的な状態に陥ってしまう。
[Prior Art] The main cause of human damage caused by recent building fires is the smoke generated. In other words, in the early stages of a fire, a large amount of smoke generated from building materials blocks visibility and delays evacuation, which eventually becomes fatal due to smoke, toxic gas, and even heat.

建物火災における従来の防煙手段として、階段などの避
難路への煙の侵入を遮断する防火ドア、又は煙の発生を
感知して外部に排気する排煙フ7ン、更にコロナ放電に
より煙粒子を帯電させて電極(一般には建物の壁面)に
吸着させる静電集塵型の消煙機などが用いられている。
Conventional smoke prevention measures for building fires include fire doors that block smoke from entering evacuation routes such as stairs, smoke exhaust fans that detect smoke generation and exhaust it to the outside, and smoke particles that are removed by corona discharge. Electrostatic precipitator-type smoke extinguishers are used that charge the dust and attract it to an electrode (generally the wall of a building).

[発明が解決しようとする課題] ところが、上記防火シャッタは単に局地的に煙を遮断す
るだけであって、煙が充満している側では視界が低下し
て呼吸が困難となる。排煙ファンにより建物各部の煙を
希望レベルまで抑圧することは装置規模の点で困難であ
り、また、燃焼部位に新鮮空気を導入してしまう不利も
ある。静電集塵型の消煙機も局部的な消煙には好適であ
るが、建物各部の消煙に対しては装置規模の点で同様に
困難である。
[Problems to be Solved by the Invention] However, the above-mentioned fire shutter merely blocks smoke locally, and visibility decreases on the smoke-filled side, making it difficult to breathe. It is difficult to suppress smoke in various parts of a building to the desired level using a smoke exhaust fan due to the scale of the device, and there is also the disadvantage of introducing fresh air into the combustion area. Electrostatic precipitator type smoke extinguishers are also suitable for localized smoke elimination, but are similarly difficult to eliminate smoke from various parts of buildings due to the scale of the device.

本発明は上記した問題に鑑みなされたものであり、火災
などによる煙が充満した場合、速やかに消煙し得る経済
的手段を提供することを、その解決すべき課題としてい
る。
The present invention has been made in view of the above-mentioned problems, and an object to be solved is to provide an economical means that can promptly extinguish smoke when the smoke is filled due to a fire or the like.

[課題を解決するための手段] 本発明の消煙装置は、室内天井部又は壁部に設けられた
噴霧ノズルと、該噴霧ノズルに0.1?−3000PP
Mの範囲で界面活性剤が添加された高圧水を供給する高
圧水供給部と、上記噴霧ノズルへの上記高圧水の供給を
制御する制御手段とを具備している。
[Means for Solving the Problems] The smoke extinguishing device of the present invention includes a spray nozzle provided on the indoor ceiling or wall, and a spray nozzle of 0.1? -3000PP
The apparatus includes a high-pressure water supply section that supplies high-pressure water to which a surfactant is added in a range of M, and a control means that controls the supply of the high-pressure water to the spray nozzle.

例えば、上記制御手段は、室内の煙濃度を検出する煙セ
ンサと、煙センサの出力信号を処理して所定値以上の煙
濃度を判別して作動信号を発する判別部と、作動信号の
入力により高圧水を噴霧ノズルに供給する弁装置とで構
成することができる。
For example, the control means may include a smoke sensor that detects the indoor smoke concentration, a determination unit that processes the output signal of the smoke sensor to determine the smoke concentration that is equal to or higher than a predetermined value, and issues an activation signal, and and a valve device that supplies high-pressure water to the spray nozzle.

また、噴霧ノズルに高電圧を印加すれば割出水滴を帯電
(一般的には正帯電〉させることができる。一般に、煙
は正又は負(一般には負)に帯電しているので、割出水
滴を逆帯電させることにより、消煙性を向上することが
できる。
In addition, by applying a high voltage to the spray nozzle, the indexed water droplets can be charged (generally positively charged).In general, smoke is positively or negatively charged (generally negative), so the indexed water droplets can be charged (generally positively charged). By reversely charging the water droplets, smoke elimination performance can be improved.

割出水滴径の多くは0.01〜5mmの範囲となってい
ることが好ましい。水滴径が上記範囲よりも大きい場合
には、水消費量に比較して消煙効果が小さく、水滴径が
上記範囲よりも小さい場合には、水滴の落下速度が小さ
く、水滴自体が煙の一部となって視界を遮る。
It is preferable that most of the diameters of the indexed water droplets are in the range of 0.01 to 5 mm. If the water droplet diameter is larger than the above range, the smoke quenching effect is small compared to the amount of water consumed, and if the water droplet diameter is smaller than the above range, the falling speed of the water droplets is small and the water droplets themselves become part of the smoke. It forms a part and blocks the view.

界面活性剤としては、カチオン性、アニオン性両性又は
ノニオン性のいずれの種類のものでもよいが、負に帯電
した煙粒子の吸着に好適なカチオン性のものがより好適
である。
The surfactant may be cationic, anionic, amphoteric or nonionic, but cationic surfactants are more suitable as they are suitable for adsorbing negatively charged smoke particles.

カチオン性界面活性剤の濃度は、1〜1100PPとす
ることが好適である。アニオン性界面活性剤の濃度は、
1〜1100PPとすることが好適である。両性界面活
性剤の濃度は、10〜3000PPMとすることが好適
である。ノニオン性界面活性剤の濃度は、10〜300
0PPMとすることが好適である。上記した範囲を外れ
ると、消煙効果は小さくなる。
The concentration of the cationic surfactant is preferably 1 to 1100 PP. The concentration of anionic surfactant is
It is suitable to set it as 1-1100PP. The concentration of the amphoteric surfactant is preferably 10 to 3000 PPM. The concentration of nonionic surfactant is 10 to 300
It is preferable to set it to 0PPM. Outside the above range, the smoke eliminating effect will be reduced.

水滴の表面張力は40dyne/cm下と、更には30
dyne/Cmとすることが好ましい。
The surface tension of water droplets is below 40 dyne/cm, and even below 30 dyne/cm.
It is preferable to set it as dyne/Cm.

表面張力が小さいほど、一般には消煙効果が向上する。The lower the surface tension, the better the smoke removal effect in general.

[作用] 制御手段が例えば煙を感知すると、高圧水供給部から噴
霧ノズルに高圧水を供給させる。煙粒子は噴霧ノズルか
ら煙中に割出された水滴に濡れく吸着して〉、共に落下
する。
[Operation] When the control means detects smoke, for example, it causes the high pressure water supply section to supply high pressure water to the spray nozzle. The smoke particles are wetly adsorbed by the water droplets released into the smoke from the spray nozzle and fall together.

水滴に0.1〜3000PPMの範囲で添加されている
界面活性剤は、その小さい表面張力又は静電的な結合力
により、煙粒子の補集性を向上させる。
A surfactant added to water droplets in a range of 0.1 to 3000 PPM improves the ability to collect smoke particles due to its small surface tension or electrostatic binding force.

[実施例コ (実施例1) 本発明の消煙装置の一実施例を第1図により説明する。[Example code] (Example 1) An embodiment of the smoke extinguishing device of the present invention will be described with reference to FIG.

この消煙装置は、建物通路消煙用のものであって、噴霧
ノズル1、高圧水供給部2、煙センサ3、判別部4、弁
装置5、高電圧電源6を備えており、煙センサ3、判別
部4、弁装置5は本発明でいう制御手段を構成している
This smoke extinguishing device is for eliminating smoke from building passageways, and includes a spray nozzle 1, a high-pressure water supply section 2, a smoke sensor 3, a discrimination section 4, a valve device 5, a high voltage power source 6, and a smoke sensor. 3, the discriminator 4 and the valve device 5 constitute a control means in the present invention.

すなわち、建物通路100の天井部分101に複数の噴
霧ノズル1が設けられており、噴霧ノズル1は配管10
及び弁装置5を介して高圧水供給部2に接続されている
。ここで、煙センサ3は電極間隙中の煙粒子をイオン化
して電極間抵抗を検出する型式のものを用いているが、
当然他の型式のものでもよい。弁装置5は電磁2方弁か
らなり、高圧水供給部2は高圧の炭酸ガス液と3PPM
のカチオン性界面活性剤が添加された水(図示せず)と
が充填されたボンベからなる。
That is, a plurality of spray nozzles 1 are provided on the ceiling portion 101 of the building passage 100, and the spray nozzles 1 are connected to the pipe 10.
and is connected to the high-pressure water supply section 2 via the valve device 5. Here, the smoke sensor 3 is of a type that ionizes smoke particles in the electrode gap and detects the resistance between the electrodes.
Of course, other types may also be used. The valve device 5 consists of an electromagnetic two-way valve, and the high-pressure water supply section 2 supplies high-pressure carbon dioxide liquid and 3PPM.
It consists of a cylinder filled with water (not shown) to which a cationic surfactant is added.

判別部4はマイコン装置からなり、煙センサ3の出力電
流を判断して煙濃度が規定レベル以上となった場合に、
作動信号を弁装置5と高電圧電源6とに出力する。
The determination unit 4 is composed of a microcomputer device, and determines the output current of the smoke sensor 3, and when the smoke concentration exceeds a specified level,
An actuation signal is output to the valve device 5 and the high voltage power supply 6.

高電圧電源6の出力端は絶縁被覆電線20により噴霧ノ
ズル1に接続されており、高電圧電源6は判別部4から
作動信号が入力された場合に噴霧ノズル1に高電圧(約
+10kV)を出力する。
The output end of the high voltage power supply 6 is connected to the spray nozzle 1 by an insulated wire 20, and the high voltage power supply 6 applies a high voltage (approximately +10 kV) to the spray nozzle 1 when an activation signal is input from the determination unit 4. Output.

なお、噴霧ノズル1はテフロンシール(図示せず〉を介
して配管10に結合されており、上記高電圧は噴霧ノズ
ル1にのみ印加される。
The spray nozzle 1 is connected to the pipe 10 via a Teflon seal (not shown), and the high voltage is applied only to the spray nozzle 1.

この消煙装置の動作を以下に説明すれば、建物通路10
0に煙が充満すると煙センサ3は煙濃度に対応する信号
を判別部4に出力し、判別部4は煙濃度が規定レベルを
超えると、弁装置2を開き噴霧ノズル1から微粒の水滴
を噴霧する。水滴は落下する途中において、煙粒子を捕
集し、建物通路100を消煙する。
The operation of this smoke extinguishing device will be explained below.
0 is filled with smoke, the smoke sensor 3 outputs a signal corresponding to the smoke concentration to the discrimination section 4, and when the smoke concentration exceeds a specified level, the discrimination section 4 opens the valve device 2 and discharges fine water droplets from the spray nozzle 1. Spray. As the water droplets fall, they collect smoke particles and eliminate smoke from the building passageway 100.

なお、水滴は正の高電位を付与されているので、一般に
負に帯電している煙粒子を静電力により捕集する。更に
、3PPMの界面活性剤が水滴に添加されているので、
界面活性剤が添り口されていない場合に比較して水滴は
煙粒子を濡らしやすくなっており、水滴の煙粒子捕集能
が格段に改善されている。これは、主として水滴の表面
張力が低下して水滴の濡らし性が向上するためであると
考えられる。
Note that since the water droplets are given a high positive potential, they collect smoke particles, which are generally negatively charged, by electrostatic force. Furthermore, since 3 PPM of surfactant is added to the water droplets,
Compared to the case where no surfactant is added, the water droplets wet the smoke particles more easily, and the ability of the water droplets to collect smoke particles is significantly improved. This is considered to be mainly because the surface tension of the water droplets is reduced and the wettability of the water droplets is improved.

噴霧ノズル3から射出される水滴の平均粒径は、噴霧圧
力とノズル形状とに依存して決定されるが、水滴径の多
くが0.01〜1mmの範囲に入るようにすることが好
ましい。
The average particle diameter of the water droplets ejected from the spray nozzle 3 is determined depending on the spray pressure and the nozzle shape, but it is preferable that most of the water droplet diameters fall within the range of 0.01 to 1 mm.

次に、界面活性剤添加の水を噴霧した場合の消煙効果を
以下に説明する。
Next, the smoke eliminating effect when spraying surfactant-added water will be explained below.

実験装置は、第3図に示すように、間口が340cm、
高さが120cm、奥行が5Qcmの密閉箱30を用い
、その互いに対面する2側壁31.31に、それぞれ小
間口32が3箇所づつ設けられている。各小開口32に
は対物レンズ(図示せず〉が装着されており、対面する
一対のレンズ対の光軸は一致している。図中、左の側壁
31の外側において各光軸上にそれぞれ発光装置34が
設けられ、同様に、右の側壁31の外側において各光軸
上にそれぞれ受光装置35が設けられている。
The experimental equipment had a frontage of 340 cm, as shown in Figure 3.
A closed box 30 with a height of 120 cm and a depth of 5 Q cm is used, and three booth openings 32 are provided in each of two side walls 31 and 31 facing each other. Each small aperture 32 is equipped with an objective lens (not shown), and the optical axes of the pair of lenses that face each other are aligned.In the figure, on the outside of the left side wall 31, each A light emitting device 34 is provided, and similarly, a light receiving device 35 is provided on each optical axis on the outside of the right side wall 31.

そして、各発光装置34は白熱電球(図示せず)を内蔵
しており、これら白熱電球から出た光は左右一対のレン
ズを通して受光装置35に入射して電流に変換される。
Each light emitting device 34 includes an incandescent light bulb (not shown), and the light emitted from the incandescent light bulb enters the light receiving device 35 through a pair of left and right lenses and is converted into an electric current.

また、密閉箱30の上部には内部に被試験液を噴霧する
噴霧ノズル36が装着されており、密閉箱30の底部に
は蚊取り線香6゜1グラムからなる電源37が設置され
ている。
Further, a spray nozzle 36 for spraying the liquid to be tested inside is attached to the top of the sealed box 30, and a power source 37 consisting of 6°1 gram of mosquito coil is installed at the bottom of the sealed box 30.

実験は、上記蚊取り線香を燃焼させ終えた後、各被試験
水を所定時間噴霧して実施した。
The experiment was conducted by spraying each test water for a predetermined period of time after the mosquito coil was burned.

なお、実験前における(煙発生前における)受光装置3
5の出力電流は’loomA(約300ルクスに相当)
に調整した。
In addition, the light receiving device 3 before the experiment (before smoke generation)
The output current of 5 is 'loomA (equivalent to about 300 lux)
Adjusted to.

出力電流(照度)はほぼ煙濃度に反比例するものと考え
られる。噴霧時間は5秒間、噴霧水量は16.5CC1
射出水滴の平均粒径は0.423mmと、0.225m
mとした。第4図〜第10図中、点線は平均粒径が0.
423mmの場合、実線は平均粒径が0.225mmの
場合である。
It is thought that the output current (illuminance) is approximately inversely proportional to the smoke density. Spray time is 5 seconds, spray water amount is 16.5 CC1
The average particle size of the ejected water droplets is 0.423 mm and 0.225 m.
It was set as m. In Figures 4 to 10, the dotted lines indicate the average particle diameter of 0.
In the case of 423 mm, the solid line is the case where the average grain size is 0.225 mm.

また、界面活性剤が添加されていない水を噴霧した場合
及びなんら噴霧しない(無噴霧の)場合についても実験
した。 時間経過にともなう上記電流の変化を示す第4
図〜第10図かられかるように、無噴霧の場合における
電流増加(視界回復〉の程度に比べて、界面活性剤を混
入しない水を噴霧しても消煙効果はほとんどない。
Further, experiments were also conducted in the case where water to which no surfactant was added was sprayed, and in the case where no water was sprayed at all (no spraying). The fourth graph shows the change in the above current over time.
As can be seen from Figures 1 to 10, spraying water without surfactant has almost no smoke eliminating effect compared to the degree of current increase (recovery of visibility) in the case of no spraying.

界面活性剤の適量混合により電流は大幅に増加する。た
だ、最大効果を奏する界面活性剤濃度は界面活性剤の種
類により大幅に異なる。すなわち、アニオン性界面活性
剤の濃度は、ネオペレックスF−25及びエマール2F
ニードル(商品名、花王株式会社製〉を用いた第4図及
び第5図かられかるように、0.1〜11000PP、
特に、10〜1100PPがよい。
The current can be significantly increased by mixing an appropriate amount of surfactant. However, the surfactant concentration that produces the maximum effect varies greatly depending on the type of surfactant. That is, the concentration of anionic surfactant was
As shown in Figures 4 and 5 using a needle (trade name, manufactured by Kao Corporation), 0.1 to 11000PP,
In particular, 10 to 1100 PP is good.

カチオン性界面活性剤の濃度は、サニゾールC及びコー
タミン24P(商品名、花王株式会社製)を用いた第7
図及び第8図かられかるように、0゜1〜11000P
P、特に、1〜1100PPがよい。更に、サニゾール
Cの方がコータミン24Pよりも優れていた。
The concentration of the cationic surfactant was determined using Sanizol C and Cortamine 24P (trade name, Kao Corporation).
As shown in Figures and Figure 8, 0°1~11000P
P, especially 1-1100PP is good. Furthermore, Sanizol C was superior to Cortamine 24P.

両性界面活性剤の濃度は、アンヒトール2ON(商品名
、花王株式会社製)を用いた第6図かられかるように、
0.1〜3000PPM、特に10〜3000PPMと
することがよい。
The concentration of the amphoteric surfactant is as shown in Figure 6 using Amphitol 2ON (trade name, manufactured by Kao Corporation).
It is preferably 0.1 to 3000 PPM, particularly 10 to 3000 PPM.

ノニオン性界面活性剤の濃度は、エマルケン120及び
エマルケン909(商品名、花王株式会社製)を用いた
第9図及び第10図かられかるように、10〜3000
PPMがよい。ノニオン性界面活性剤の場合には110
PPといった低濃度領域と11000PPといった高濃
度領域において効果が高く、双峰特性を有している。
The concentration of the nonionic surfactant is 10 to 3000 as shown in Figures 9 and 10 using Emulken 120 and Emulken 909 (trade name, manufactured by Kao Corporation).
PPM is good. 110 for nonionic surfactants
It is highly effective in a low concentration region such as PP and a high concentration region such as 11000PP, and has bimodal characteristics.

次に、カチオン性界面活性剤であるサニゾールCを用い
、射出水滴の平均粒径を約0.1mmに縮小した場合に
ついて実験結果を第11図に示す。
Next, FIG. 11 shows the experimental results for the case where the average particle size of the injected water droplets was reduced to about 0.1 mm using Sanizol C, which is a cationic surfactant.

噴霧水量は約16.50Cとしたままで噴霧時間は26
秒間に延長した。この場合、割出水滴の平均粒径が微小
であるために、電流は噴霧直後に低下しその後、水滴の
凝集、沈降とともに回復することがわかった。この実験
結果から、射出水滴の平均粒径は少なくとも約0.1m
m以上であれば有効であることがわかる。
The spray water amount was kept at about 16.50C and the spray time was 26.
Extended to seconds. In this case, it was found that because the average particle size of the indexed water droplets was minute, the current decreased immediately after spraying and then recovered as the water droplets coagulated and settled. From this experimental result, the average particle size of the ejected water droplets is at least about 0.1 m.
It can be seen that it is effective if it is greater than or equal to m.

次に、サニゾールCを用い、噴霧時間は5秒間、噴霧水
量は16.50Cのままとし、噴霧ノズル36の形状を
、市販のスプリンクラ−のものに代えた場合について第
12図〜第13図に示す。
Next, Figures 12 and 13 show the case where Sanizol C is used, the spray time is 5 seconds, the spray water amount is kept at 16.50C, and the shape of the spray nozzle 36 is changed to that of a commercially available sprinkler. show.

第12図は割出水滴の平均粒径を約0.225mmとし
た場合、第13図は割出水滴の平均粒径を約0.423
mmとした場合である。その結果、噴霧ノズル36の変
更にかかわらず、同様の結果を得た。
Figure 12 shows the average particle size of the indexed water droplets is about 0.225 mm, and Figure 13 shows the average particle size of the indexed water droplets of about 0.423 mm.
This is the case when it is set as mm. As a result, similar results were obtained regardless of the change in the spray nozzle 36.

次に、界面活性剤型7In水及び非添加水の表面張力と
照度変化との関係を第14図に示す。
Next, FIG. 14 shows the relationship between the surface tension of surfactant-type 7In water and non-additive water and illuminance changes.

ただし、射出水滴の平均粒径は約0.178mm、噴霧
水量は16.5CC1噴霧時間は5秒問とした。なお、
噴霧直前の照度は4Qlxである。
However, the average particle size of the ejected water droplets was approximately 0.178 mm, the amount of water sprayed was 16.5 CC, and the spray time was 5 seconds. In addition,
The illuminance immediately before spraying is 4Qlx.

更に、界面活性剤非添加水の場合も参考に示す。Furthermore, the case of water without surfactant added is also shown for reference.

第14図かられかるように、水滴の表面張力が小ざいほ
ど、照度増加効果すなわち視界改善効果がより早く示現
する。
As can be seen from FIG. 14, the smaller the surface tension of the water droplets, the faster the illuminance increasing effect, that is, the visibility improving effect appears.

以上の実験結果より更に以下のことが判明した。The above experimental results further revealed the following.

すなわち、カチオン性界面活性剤のサニゾールCが良い
消煙効果をもつ。これは、煙粒子が一般に負に帯電する
ため、正に荷電したカチオン性界面活性剤と引合って吸
着効果を向上させるからであると考えられる。
That is, Sanizol C, a cationic surfactant, has a good smoke eliminating effect. This is thought to be because smoke particles are generally negatively charged and attract the positively charged cationic surfactant to improve the adsorption effect.

更に、アニオン性界面活性剤及びカチオン性界面活性剤
では、ベンゼン環を有するもの(例えば第7図に示すサ
ニゾールC〉の消煙効果がそれを持たないもの(例えば
第8図に示すコータミン24P)に対して優れているこ
とも判明した。
Furthermore, among anionic surfactants and cationic surfactants, those with a benzene ring (for example, Sanizol C shown in Figure 7) have a smoke eliminating effect, but those without it (for example, Cortamine 24P shown in Figure 8) It was also found that it is superior to

(第2実施例〉 本発明の消煙装置の他の実施例を第2図に示す。(Second example) Another embodiment of the smoke eliminating device of the present invention is shown in FIG.

この消煙装置は、噴霧ノズル1aと高圧水供給部2aと
弁装置5aと配管10aと高電圧電源6aとを防火ドア
300に内蔵した点を除いて、実施例1のものと同じ構
成を有している。
This smoke extinguisher has the same configuration as that of Example 1, except that the spray nozzle 1a, high-pressure water supply section 2a, valve device 5a, piping 10a, and high-voltage power supply 6a are built into the fire door 300. are doing.

噴霧ノズル1aは防火ドア300の両側面上部に複数個
設けられており、高圧水供給部2aは防火ドア300の
肉厚に合わせて形成された薄肉タンクからなる。
A plurality of spray nozzles 1a are provided at the upper portions of both sides of the fire door 300, and the high-pressure water supply section 2a consists of a thin tank formed to match the wall thickness of the fire door 300.

この消煙装置の動作は基本的に実施例1のものと同じで
あり、図示しない煙センサから出力される煙濃度信号に
より作動する。
The operation of this smoke eliminator is basically the same as that of the first embodiment, and is activated by a smoke concentration signal output from a smoke sensor (not shown).

ただ、この消煙装置では、判別部(図示せず)が出す作
動信号は防火ドア300のドア係止解除部(図示せず〉
にも出力され、このドア係止解除部は防火ドア300を
閉鎖する。
However, in this smoke extinguishing device, the activation signal issued by the discriminator (not shown) is sent to the door unlocking part (not shown) of the fire door 300.
This door lock release unit closes the fire door 300.

したがって、この実施例では既存の防火ドアに一部構成
要素を付加するだけで防火ドア周辺の消煙が可能となり
、防火ドア300の視認性を簡単に向上させることがで
きる。
Therefore, in this embodiment, smoke can be extinguished around the fire door by simply adding some components to the existing fire door, and the visibility of the fire door 300 can be easily improved.

実施例3 第3実施例の消煙装置を第15図に示す。Example 3 A smoke eliminator according to a third embodiment is shown in FIG.

この消煙装置は、実施例1の消煙装置(第1図参照〉に
おいて噴霧ノズル、弁装置、高圧水供給部及び高電圧電
源をそれぞれ2種類設けたものであり、第1の高圧水供
給部31は第1の弁装置51を介して第1の噴霧ノズル
32にカチオン性界面活性剤添加水を供給し、第2の高
圧水供給部33は第2の弁装置52を介して第2の噴霧
ノズル34にアニオン性界面活性剤添加水を供給し、第
1の噴霧ノズル32はより小さな平均粒径(約0゜1m
m>をもつ水滴を噴霧し、第2の噴霧ノズル34はより
大きな平均粒径(約0.7mm>をもつ水滴を噴霧する
。そして、第1の高電圧電源61は第1の噴霧ノズルに
正の高電圧を印カロし、第2の高電圧電源62は第2の
噴霧ノズルに負の高電圧を印力Ofる。なお、水滴の平
均粒径は周知のようにノズル構造及び水圧により決定さ
れる。
This smoke extinguishing device is the same as the smoke extinguishing device of Example 1 (see Fig. 1), but has two types of spray nozzles, valve devices, high-pressure water supply parts, and high-voltage power sources, and the first high-pressure water supply The section 31 supplies cationic surfactant-added water to the first spray nozzle 32 via the first valve device 51 , and the second high-pressure water supply section 33 supplies the second water to the first spray nozzle 32 via the second valve device 52 . The anionic surfactant-added water is supplied to the first spray nozzle 34, and the first spray nozzle 32 has a smaller average particle size (approximately 0°1 m).
m>, and the second spray nozzle 34 sprays water droplets with a larger average particle diameter (approximately 0.7 mm>).The first high voltage power supply 61 then connects the first spray nozzle to A positive high voltage is applied, and the second high voltage power supply 62 applies a negative high voltage to the second spray nozzle.As is well known, the average particle size of the water droplets depends on the nozzle structure and water pressure. It is determined.

このようにすると、一般に負に帯電する煙粒子は微小な
カチオン性界面活性剤添加水滴に良好に吸着され、そし
て、カチオン性界面活性剤添加水滴は平均粒径がより大
きく沈降速度がより大きなアニオン性界面活性剤添加水
滴に吸着される。したがって、カチオン性界面活性剤添
加水滴を微小化してその合計表面積を増加し更にその正
電荷を分散して、煙粒子を良好に吸着することができる
In this way, the smoke particles, which are generally negatively charged, are well adsorbed by the minute cationic surfactant-added water droplets, and the cationic surfactant-added water droplets have a larger average particle size and a higher sedimentation rate than the anion particles. The surfactant is adsorbed onto the water droplets. Therefore, the cationic surfactant-added water droplets can be miniaturized to increase their total surface area and further disperse their positive charges, thereby making it possible to adsorb smoke particles well.

なお、アニオン性界面活性剤添加水をカチオン性界面活
性剤添加水よりも遅く噴霧すれば、カチオン性界面活性
剤添加水滴が充分に煙粒子を吸着した後で、アニオン性
界面活性剤添加水滴がカチオン性界面活性剤添加水滴を
吸着、沈降させることができる。
Note that if the anionic surfactant-added water is sprayed later than the cationic surfactant-added water, the anionic surfactant-added water droplets will be released after the cationic surfactant-added water droplets have sufficiently adsorbed smoke particles. Cationic surfactant-added water droplets can be adsorbed and precipitated.

[発明の効果コ 上記説明したように、本発明の消煙装置は噴霧ノズルか
ら0.1〜3000PPMの界面活性剤を添加した水を
噴霧して消煙するので、室内火災において人的被害を格
段に減少することができる。
[Effects of the Invention] As explained above, the smoke extinguishing device of the present invention eliminates smoke by spraying water to which 0.1 to 3000 PPM of surfactant is added from the spray nozzle, thereby reducing human damage in indoor fires. can be significantly reduced.

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

第1図は第1実施例の消煙装置を示すブロック図、第2
図は第2実施例の消煙装置を示す斜視図、第3図は実験
装置を示す断面図、第4図〜第13図は各種界面活性剤
添加水の噴霧による視界回復実験の結果を示す電流(視
界〉−時開特性図、第14図は各種界面活性剤添加水の
噴霧による視界回復実験における各種界面活性剤添加水
の表面張力値の影響を示す特性図、第15図は第3実施
例の消煙装置を示すブロック図である。 1・・・噴霧ノズル 2・・・高圧水供給部 3・・・煙センサ(制御手段) 4・・・制御部(制御手段〉 5・・・弁装置(制御手段〉
Fig. 1 is a block diagram showing the smoke extinguishing device of the first embodiment;
The figure is a perspective view showing the smoke extinguishing device of the second embodiment, Figure 3 is a sectional view showing the experimental equipment, and Figures 4 to 13 show the results of visibility recovery experiments by spraying various types of surfactant-added water. Current (visual field) - time-varying characteristic diagram, Figure 14 is a characteristic diagram showing the influence of surface tension values of various surfactant-added waters in visibility recovery experiments by spraying various surfactant-added waters, and Figure 15 is the third It is a block diagram showing a smoke extinguishing device of an example. 1... Spray nozzle 2... High pressure water supply part 3... Smoke sensor (control means) 4... Control part (control means>) 5...・Valve device (control means)

Claims (4)

【特許請求の範囲】[Claims] (1)室内天井部又は壁部に設けられた噴霧ノズルと、
該噴霧ノズルに0.1〜3000PPMの範囲で界面活
性剤が添加された高圧水を供給する高圧水供給部と、上
記噴霧ノズルへの上記高圧水の供給を制御する制御手段
とを具備してなる消煙装置。
(1) A spray nozzle installed on the indoor ceiling or wall;
A high-pressure water supply section that supplies high-pressure water to the spray nozzle with a surfactant added in a range of 0.1 to 3000 PPM, and a control means that controls the supply of the high-pressure water to the spray nozzle. A smoke extinguishing device.
(2)上記制御手段は、室内の煙濃度を検出する煙セン
サと、該煙センサの出力信号を処理して所定値以上の煙
濃度を判別して作動信号を発する判別部と、上記作動信
号の入力により上記高圧水を上記噴霧ノズルに供給する
弁装置とを備えている請求項1記載の消煙装置。
(2) The control means includes a smoke sensor that detects the smoke concentration in the room, a determination section that processes the output signal of the smoke sensor to determine the smoke concentration that is equal to or higher than a predetermined value, and issues an activation signal; 2. The smoke extinguishing device according to claim 1, further comprising a valve device that supplies the high-pressure water to the spray nozzle upon input of the above.
(3)上記噴霧ノズルに高電圧を印加する高電圧電源を
備えている請求項1記載の消煙装置。
(3) The smoke extinguishing device according to claim 1, further comprising a high voltage power source that applies a high voltage to the spray nozzle.
(4)上記噴霧ノズル及び上記高圧水供給部はそれぞれ
2種類設けられており、上記第1の高圧水供給部は上記
第1の噴霧ノズルにカチオン性界面活性剤添加水を供給
し、上記第2の高圧水供給部は上記第2の噴霧ノズルに
アニオン性界面活性剤添加水を供給し、上記第2の噴霧
ノズルは上記第1の噴霧ノズルよりも大きな平均粒径を
もつ水滴を噴霧するものである請求項1記載の消煙装置
(4) Two types of the above-mentioned spray nozzle and the above-mentioned high-pressure water supply section are provided, and the above-mentioned first high-pressure water supply section supplies cationic surfactant-added water to the above-mentioned first spray nozzle, and the above-mentioned first high-pressure water supply section supplies cationic surfactant-added water to the above-mentioned first spray nozzle. The second high-pressure water supply unit supplies anionic surfactant-added water to the second spray nozzle, and the second spray nozzle sprays water droplets having a larger average particle size than the first spray nozzle. The smoke extinguisher according to claim 1, which is a smoke extinguisher.
JP32779789A 1989-12-18 1989-12-18 Smoke extinguishing device Pending JPH03186276A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP32779789A JPH03186276A (en) 1989-12-18 1989-12-18 Smoke extinguishing device
US08/111,399 US5353879A (en) 1989-12-18 1993-08-25 Door having smoke reducing apparatus associated therewith

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP32779789A JPH03186276A (en) 1989-12-18 1989-12-18 Smoke extinguishing device

Publications (1)

Publication Number Publication Date
JPH03186276A true JPH03186276A (en) 1991-08-14

Family

ID=18203103

Family Applications (1)

Application Number Title Priority Date Filing Date
JP32779789A Pending JPH03186276A (en) 1989-12-18 1989-12-18 Smoke extinguishing device

Country Status (1)

Country Link
JP (1) JPH03186276A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH114905A (en) * 1997-04-23 1999-01-12 Bunka Shutter Co Ltd Device and method for fire extinguishing and smoke absorbing using water mist
JP2009106405A (en) * 2007-10-29 2009-05-21 Hochiki Corp Fire prevention equipment and spraying method
WO2009107421A1 (en) * 2008-02-28 2009-09-03 ホーチキ株式会社 Nozzle head device for firefighting
WO2010082349A1 (en) * 2009-01-19 2010-07-22 ホーチキ株式会社 Fire disaster prevention facility and spraying method
JP2012183319A (en) * 2012-04-23 2012-09-27 Hochiki Corp Charging sprinkler head
TWI383815B (en) * 2008-12-24 2013-02-01 Hochiki Co Fire and disaster prevention equipment, spraying methods, spray air-conditioning equipment and spray methods
TWI564054B (en) * 2008-12-24 2017-01-01 Hochiki Co Fire and disaster prevention equipment and spray air-conditioning equipment charged spray head

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4932494A (en) * 1972-07-24 1974-03-25
JPS548017A (en) * 1977-06-17 1979-01-22 Brother Ind Ltd Serial printer
JPS58174258A (en) * 1982-04-05 1983-10-13 Minato Seiyaku Kk Generator for electrified and atomized particle or electrostatic removal of smoke
JPS6334446B2 (en) * 1983-09-27 1988-07-11 Mitsubishi Electric Corp

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4932494A (en) * 1972-07-24 1974-03-25
JPS548017A (en) * 1977-06-17 1979-01-22 Brother Ind Ltd Serial printer
JPS58174258A (en) * 1982-04-05 1983-10-13 Minato Seiyaku Kk Generator for electrified and atomized particle or electrostatic removal of smoke
JPS6334446B2 (en) * 1983-09-27 1988-07-11 Mitsubishi Electric Corp

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH114905A (en) * 1997-04-23 1999-01-12 Bunka Shutter Co Ltd Device and method for fire extinguishing and smoke absorbing using water mist
JP2009106405A (en) * 2007-10-29 2009-05-21 Hochiki Corp Fire prevention equipment and spraying method
US8776902B2 (en) 2007-10-29 2014-07-15 Hochiki Corporation Fire prevention equipment and spraying method
WO2009107421A1 (en) * 2008-02-28 2009-09-03 ホーチキ株式会社 Nozzle head device for firefighting
US8181710B2 (en) 2008-02-28 2012-05-22 Hochiki Corporation Tube-end device for fire extinguishment
EP2258449A4 (en) * 2008-02-28 2015-08-05 Hochiki Co Nozzle head device for firefighting
EP2258449B1 (en) * 2008-02-28 2019-01-02 Hochiki Corporation Nozzle head device for firefighting
TWI383815B (en) * 2008-12-24 2013-02-01 Hochiki Co Fire and disaster prevention equipment, spraying methods, spray air-conditioning equipment and spray methods
TWI564054B (en) * 2008-12-24 2017-01-01 Hochiki Co Fire and disaster prevention equipment and spray air-conditioning equipment charged spray head
WO2010082349A1 (en) * 2009-01-19 2010-07-22 ホーチキ株式会社 Fire disaster prevention facility and spraying method
US8413735B2 (en) 2009-01-19 2013-04-09 Hochiki Corporation Fire prevention equipment and spraying method
JP2012183319A (en) * 2012-04-23 2012-09-27 Hochiki Corp Charging sprinkler head

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