JP2009090194A - Scavenger of smoke aerosol in enclosed space, its apparatus and method for scavenging smoke aerosol in closed space using its apparatus - Google Patents

Scavenger of smoke aerosol in enclosed space, its apparatus and method for scavenging smoke aerosol in closed space using its apparatus Download PDF

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JP2009090194A
JP2009090194A JP2007262303A JP2007262303A JP2009090194A JP 2009090194 A JP2009090194 A JP 2009090194A JP 2007262303 A JP2007262303 A JP 2007262303A JP 2007262303 A JP2007262303 A JP 2007262303A JP 2009090194 A JP2009090194 A JP 2009090194A
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smoke
smoke aerosol
aerosol
closed space
aqueous solution
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Nobuo Kobayashi
暢生 小林
Yoshiyuki Hayashi
良之 林
Yasumasa Numata
恭政 沼田
Yasushi Nakaida
靖 中井田
Reiko Kobayashi
禮子 小林
Taiichiro Yoshida
泰一郎 吉田
Shin Nakae
慎 中江
Shuji UCHIDA
周治 内田
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ESPO CHEMICAL CORP
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a chemical agent, an apparatus and a method which quickly eliminate and detoxify smoke or the like in a fire in an enclosed apace and have conventionally not met effective technologies. <P>SOLUTION: A scavenger of a smoke aerosol in an enclosed space which has a relative humidity of 60% or lower and contains a hygroscopic compound aqueous solution saturated or with 30% or higher saturation at a room temperature, an apparatus for scavenging a smoke aerosol in an enclosed space which is provided with a vapor-liquid contact layer (A) made of a hydrophilic particle porous material impregnated with this scavenger, and a method for scavenging a smoke aerosol in an enclosed space using this eliminating apparatus are disclosed. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、外気の流入がほとんどないか限られている閉鎖空間(以下、閉鎖空間という)、及びトンネル内の自動車道(以下トンネル内という)の煙、さらに随伴する煙以外の有害気体や有害エアロゾルの除去剤、除去装置及び除去方法に関する。 The present invention relates to a closed space (hereinafter referred to as a closed space) where there is little or no inflow of outside air, smoke from a motorway in a tunnel (hereinafter referred to as a tunnel), and harmful gases and harmful gases other than the accompanying smoke. The present invention relates to an aerosol remover, a removal apparatus, and a removal method.

汚染気体、特に汚染空気の清浄化法として、バグフィルタ−法、電気集塵法、種々の燃焼法、光触媒法、微生物分解法、粒状活性炭の通過/接触法、水性薬液による洗浄法などが広く実施されているが、これらの方法は、火災及びトンネル内の自動車道の煙及びその他の有害随伴物の同時分離には全く効果がなかった。
しかし閉鎖空間の火災の煙と特定しない、煙の場合、相対湿度が約70%以下、好ましくは60%以下の解放空間内の煙及びその他の有害随伴物の除去に関して、例えば特許文献1で示された薬剤による噴霧法が提案され、既に実用化されているが、この方法では水性薬液の噴霧により相対湿度が急上昇する閉鎖空間内では、消煙効果がなくなる欠点があった。長いトンネル内の排煙も同一原理の排気法が採用されているが大気汚染の原因の一つとなっている。
これ以外の実用性のある唯一の伝統的な方法は、煙が充満した閉鎖空間内に排気ポンプに直結した排煙管で煙及びその他の有害随伴物を吸引し、そのまま外部に放出する方法であった。
しかし、閉鎖空間に充満する煙により、視野を失ない脱出できず、内外で殉職する消防士や火災遭遇者の犠牲者が極めて多数であることは、このような排煙法の限界を示している。また長距離のトンネル内に充満する自動車の排煙や有機気体の除去は、通行者の健康に悪影響を及ぼし、トンネル内の火災で多くの犠牲者が発生した多くの記録がある。
特開平2−149310号公報
As a method for cleaning polluted gases, especially polluted air, there are a wide variety of methods such as bag filter method, electrostatic precipitating method, various combustion methods, photocatalyst method, microbial decomposition method, granular activated carbon passage / contact method, and aqueous chemical cleaning method. Although practiced, these methods were completely ineffective for simultaneous separation of fire and motorway smoke in tunnels and other harmful accompaniments.
However, in the case of smoke not specified as fire smoke in a closed space, the removal of smoke and other harmful companions in an open space having a relative humidity of about 70% or less, preferably 60% or less is disclosed in Patent Document 1, for example. A spray method using the prepared drug has been proposed and has already been put to practical use. However, this method has a drawback that the smoke-removing effect is lost in a closed space where the relative humidity rapidly rises due to the spray of the aqueous chemical solution. Smoke in long tunnels is one of the causes of air pollution, although the same principle exhaust method is adopted.
The only other traditional method that is practical is to suck the smoke and other harmful accompaniments through a flue pipe directly connected to the exhaust pump in a smoke-filled closed space and discharge it to the outside as it is. there were.
However, the smoke that fills the enclosed space cannot be escaped without losing sight, and the extremely large number of victims of firefighters and fire encounters at home and abroad indicate the limitations of such smoke emission methods. Yes. Also, the smoke and removal of organic gases from automobiles filling long-distance tunnels have negative effects on the health of passers-by, and there are many records of fires in the tunnel causing many casualties.
JP-A-2-149310

本発明は、従来有効な技術が存在しなかった閉鎖空間内の火災の煙などを速やかに該空間から除去・解毒する薬剤、装置及び方法を提供しようとするものである。 The present invention is intended to provide a medicine, a device, and a method for quickly removing and detoxifying fire smoke and the like in a closed space where there has been no effective technique.

本発明者らは、上記した種々の汚染空気の清浄化法の転用によって、閉鎖空間での煙の除去について内外の成功例が全くないことを調査の上で確認し、下記のような仮説をたてた。そして種々の消煙実験を行なった結果、本発明を完成させるに至ったものである。
すなわち本発明は、密閉空間での相対湿度が60%以下であり、常温で飽和又は飽和濃度の30%以上の濃度の吸湿性化合物水溶液を含有することを特徴とする閉鎖空間内の煙エアロゾルの除去剤を提供するものである。また本発明は、密閉空間での相対湿度が60%以下であり、常温で飽和又は飽和濃度の30%以上の濃度の吸湿性化合物水溶液を含有する煙エアロゾルの除去剤を含浸させた親水性の粒状多孔性物質からなる気液接触層(A)を備えることを特徴とする閉鎖空間内の煙エアロゾル除去装置を提供するものである。さらに本発明は、密閉空間での相対湿度が60%以下であり、常温で飽和又は飽和濃度の30%以上の濃度の吸湿性化合物水溶液を含有する煙エアロゾルの除去剤を含浸させた親水性の粒状多孔性物質からなる気液接触層(A)を備え、その上部に空気の吸気口(B)を備え、前記気液接触層(A)の下部に10cm以上分離して液溜層(D)を備えたエアロゾル除去装置に、前記装置外に設置した吸排気ポンプ(C)を結合し、前記吸排気ポンプ(C)により煙エアロゾルを含む空気を吸気口(B)から吸入し、前記気液接触層(A)に接触通過させることを特徴とする、閉鎖空間内の煙エアロゾルを除去する方法を提供するものである。
The present inventors have confirmed through research that there are no successful internal and external examples of smoke removal in a closed space by diverting the various cleaning methods for contaminated air described above. Established. As a result of conducting various smoke eliminating experiments, the present invention has been completed.
That is, the present invention provides a smoke aerosol in a closed space characterized by containing a hygroscopic compound aqueous solution having a relative humidity in a sealed space of 60% or less and saturated or a saturated concentration of 30% or more at normal temperature. A removal agent is provided. Further, the present invention provides a hydrophilic air impregnated with a smoke aerosol remover containing a hygroscopic compound aqueous solution having a relative humidity in a sealed space of 60% or less and a saturated or saturated concentration of 30% or more at room temperature. An apparatus for removing smoke aerosol in a closed space, comprising a gas-liquid contact layer (A) made of a granular porous material. Further, the present invention provides a hydrophilic air impregnated with a smoke aerosol remover containing a hygroscopic compound aqueous solution having a relative humidity in a sealed space of 60% or less and a saturated or saturated concentration of 30% or more at room temperature. A gas-liquid contact layer (A) made of a granular porous material is provided, an air inlet (B) is provided on the upper part thereof, and a liquid reservoir layer (D) is separated by 10 cm or more below the gas-liquid contact layer (A). ) Is connected to an intake / exhaust pump (C) installed outside the apparatus, and the intake / exhaust pump (C) sucks air containing smoke aerosol from the intake port (B). The present invention provides a method for removing smoke aerosol in a closed space, characterized in that the liquid contact layer (A) is passed through.

本発明者が立てた前記仮説は次のとおりである。
すなわち本発明者らは、「閉鎖空間内での火災の煙の消煙において、発煙筒や火災初期のくすぶり段階で発生する粒径の小さい白い煙は、表面が強く酸化されて、強い親水性基を含み、さらに燃焼による水分が水和水として強固に結合しているため、ほとんど親和性がない界面活性剤水溶液や化学反応型洗浄剤による公知の水性洗浄法では煙を除去できない。また、環状炭化水素基を含む有機化合物を不完全燃焼させた時に発生する粒径が大きく凝集した黒い煙粒子も同様にかなり親水性で水和水が強固に結合しているため、公知の方法では煙を除去できない。これらの煙を除去するためには、これらの煙に結合している水和水を煙粒子から除去する必要がある。このためには、強力な除湿剤、例えば密閉容器の底に入れるとその上部の空間が常温で安定した低相対湿度を保てる薬剤の飽和水溶液の使用が最適である。」と仮説を立てた。
そして本発明者は種々実験を行うことによりこの仮説の正しさを確認した。
The hypothesis established by the present inventor is as follows.
That is, the present inventors have stated that, in the smoke extinguishing of fire smoke in a closed space, white smoke with a small particle diameter generated in the smoke cylinder and the smoldering stage in the early stage of the fire is strongly oxidized and strongly hydrophilic. In addition, since moisture due to combustion is firmly bonded as hydrated water, smoke cannot be removed by a known aqueous cleaning method using a surfactant aqueous solution or a chemical reaction type cleaning agent having almost no affinity. Black smoke particles with large particle sizes and agglomerated when organic compounds containing cyclic hydrocarbon groups are incompletely combusted are also quite hydrophilic and hydrated water is tightly bound. In order to remove these smokes, it is necessary to remove the water of hydration that is bound to these smokes from the smoke particles. If you put it in the space above it Use of a saturated aqueous solution of agents maintain a stable low relative humidity at room temperature is optimal. "Said hypothesized.
The present inventor confirmed the correctness of this hypothesis through various experiments.

本発明の煙エアロゾル除去剤は、気液接触材に含浸した後、濃厚な煙などを含む有害気体を送風機で吸引して通過させると、煙などを高率で除去・解毒して火災室内又は室外に排気し、室内の視野を回復して脱出方向を示すため、煙による死亡事故の減少に寄与する。
本発明の煙エアロゾル除去剤は、解毒剤を含ませることにより、煙などのほかに、同時に随伴する主な有害気体をも解毒することができる。
また本発明の装置を地下室、ホテル客室の廊下、旅客機、艦船など狭い空間用には単相電源と延長コ−ドを使用する可搬式の装置として使用することができ、また空港検疫所、地下鉄構内、大容量倉庫、山中や地下トンネルの自動車道等には、大風量、定置型大型装置として使用することができるので、大規模火災時での利用が期待できる。
The smoke aerosol removing agent of the present invention, after impregnating the gas-liquid contact material, when sucking and passing harmful gases including rich smoke with a blower, removes and detoxifies smoke at a high rate, or in a fire or It exhausts to the outside and restores the field of view of the room to indicate the direction of escape, contributing to the reduction of fatal accidents.
By including the antidote, the smoke aerosol removing agent of the present invention can detoxify not only smoke but also the accompanying harmful gases.
In addition, the device of the present invention can be used as a portable device using a single-phase power source and an extension cord for a narrow space such as a basement, a corridor of a hotel guest room, a passenger plane, a ship, and an airport quarantine station, subway It can be used as a large air volume and stationary large equipment on campuses, large-capacity warehouses, highways in mountains, underground tunnels, etc., so it can be expected to be used in a large-scale fire.

本発明は、密閉空間での相対湿度が60%以下であり、常温で飽和又は飽和濃度の30%以上の濃度の吸湿性化合物水溶液を含有する閉鎖空間内の煙エアロゾルの除去剤(以下煙除去剤という)に関するものである。
本発明に使用する吸湿性化合物としては、例えば水酸化ナトリウム、水酸化カリウム、塩化リチウム、臭化リチウム、臭化カルシウム、臭化亜鉛、塩化マグネシウム、ヨウ化リチウム、ヨウ化ナトリウム、ヨウ化カリウム、酢酸カリウム、塩化カルシウム、塩化マグネシウム、燐酸、食塩と硝酸と硝酸ナトリウムとの混合物等が挙げられる。これらのうち、刺激性や強い腐食性がなく、環境に放流しても悪影響が低いもので特に消煙効果の点で、塩化カルシウム、酢酸カリウム、塩化マグネシウム及びこれらの混合物が好ましい。
吸湿性化合物水溶液の相対湿度が60%以下であれば、閉鎖空間での火災時などの煙エアロゾルを有効に除去することができる。相対湿度は、低いほど煙除去効果は優れる。吸湿性化合物水溶液が飽和濃度の時に相対湿度と消煙効果は最高になるので、できるだけ高濃度の水溶液を使用することが好ましい。すなわち吸湿性化合物水溶液は常温での飽和濃度の30%以上の濃度の水溶液で使用する。
The present invention provides a removal agent for smoke aerosol (hereinafter referred to as smoke removal) in a closed space containing a hygroscopic compound aqueous solution having a relative humidity in a sealed space of 60% or less and saturated or a saturated concentration of 30% or more at normal temperature. (Referred to as an agent).
Examples of the hygroscopic compound used in the present invention include sodium hydroxide, potassium hydroxide, lithium chloride, lithium bromide, calcium bromide, zinc bromide, magnesium chloride, lithium iodide, sodium iodide, potassium iodide, Examples include potassium acetate, calcium chloride, magnesium chloride, phosphoric acid, a mixture of sodium chloride, nitric acid and sodium nitrate. Of these, calcium chloride, potassium acetate, magnesium chloride and mixtures thereof are preferred because they have no irritation and strong corrosivity, and have a low adverse effect even when released into the environment, and particularly in terms of smoke-fusing effect.
If the relative humidity of the hygroscopic compound aqueous solution is 60% or less, it is possible to effectively remove smoke aerosol during a fire in a closed space. The lower the relative humidity, the better the smoke removal effect. When the hygroscopic compound aqueous solution has a saturated concentration, the relative humidity and the smoke eliminating effect are maximized. Therefore, it is preferable to use an aqueous solution having a concentration as high as possible. That is, the hygroscopic compound aqueous solution is used as an aqueous solution having a concentration of 30% or more of the saturation concentration at room temperature.

また本発明は、前記吸湿性化合物水溶液を含有する煙除去剤を含浸させた親水性の粒状多孔性物質からなる気液接触層(A)を備える閉鎖空間内の煙エアロゾル除去装置(以下煙除去装置という)に関するものである。
本発明に使用する粒状多孔性物質としては、耐水性紙質粒子、親水性の弾性連続気泡発泡体、親水性の吸水性活性炭、観賞用植物の土壌に混合される吸水性セラミック等が挙げられ、これらが好ましいものである。
The present invention also provides a smoke aerosol removal device (hereinafter referred to as smoke removal) in a closed space comprising a gas-liquid contact layer (A) comprising a hydrophilic granular porous material impregnated with a smoke removal agent containing the hygroscopic compound aqueous solution. Device).
Examples of the granular porous material used in the present invention include water-resistant paper particles, hydrophilic elastic open-cell foams, hydrophilic water-absorbing activated carbon, water-absorbing ceramics mixed with ornamental plant soil, and the like. These are preferred.

本発明で使用する耐水性紙質粒子とは、セルローズ質繊維の乾燥粉末から形成されたものに、耐水・耐薬品性と形状記憶性を与えたものである。例えばパルプ繊維の乾燥粉末を高速回転板容器に入れ、薄い糊液や水を滴下し、繊維を絡ませ、造粒・乾燥し、これをホルマール化して製造することができる。耐水性を付与していない未処理紙粒は、水中で振動・撹拌すると簡単に崩壊するので、本発明の粒状多孔性物質として使用するには適さない。
セルローズ質繊維としては、パルプ、綿、レーヨンなどが挙げられる。紙粒の直径は、特に制限されないが、3〜10mmの範囲が適している。さらに、紙の強度を低下させず、汚染気体の吸着・保水機能を低下させない範囲で、繊維に他の物質を混入することができる。
本発明の実施例・参考例の実験で使用した紙粒97粒平均の形状は下記表−1の形状の不規則な楕円体であり、吸湿性化合物水溶液中に浸漬して、マグネチックスタラ−で10日間撹拌しても崩壊・変形せず原形を維持した。乾燥した耐水処理紙粒1Lの個数:約5,980粒で、見掛け比重は約0.2である。
The water-resistant paper-based particles used in the present invention are obtained by giving water / chemical resistance and shape memory to a cellulosic fiber dry powder. For example, a dry powder of pulp fiber is put into a high-speed rotating plate container, a thin paste solution or water is dropped, the fibers are entangled, granulated and dried, and formalized to produce. Untreated paper grains not imparted with water resistance are not suitable for use as the granular porous material of the present invention because they easily disintegrate when vibrated and stirred in water.
Cellulose fibers include pulp, cotton, rayon and the like. The diameter of the paper grain is not particularly limited, but a range of 3 to 10 mm is suitable. Furthermore, it is possible to mix other substances into the fiber as long as the strength of the paper is not lowered and the adsorption / water retention function of the polluting gas is not lowered.
The average shape of the 97 paper grains used in the experiments of the examples and reference examples of the present invention is an irregular ellipsoid having the shape shown in Table 1 below, immersed in an aqueous hygroscopic compound solution, and magnetic stirrer. Even after stirring for 10 days, the original shape was maintained without disintegration or deformation. The number of dried water-resistant treated paper grains 1L: about 5,980, and the apparent specific gravity is about 0.2.

Figure 2009090194
Figure 2009090194

紙質粒子に耐水性を付与する方法としては、気相ホルマ−ル化処理する方法、ジメチロ−ルエチレン尿素、ポリ(メタ)アクリルアミドのメチロール化物など繊維素架橋剤により処理する方法、ポリアクリル酸塩により処理する方法等が挙げられる。
気相ホルマ−ル化処理する方法は、乾燥した紙粒を密閉室内でホルムアルデヒドガスにより部分的にホルマ−ル化して、耐水・耐薬品性と形状記憶性を与えたものである。本処理紙粒を105℃×1時間の乾燥後に湿度80%で2日間放置後の吸湿率は7.75%(n:5)であったが、未処理紙粒は9.56%であり、本処理による吸水率低下は約20%であった。また耐水化紙粒を、水で完全に含浸し、ナイロンフィラメント製網状袋に入れて消煙器に収納し、積層高さ約30cmで1時間吸収した水を台座の水平の金網の下に滴下させた後の抱水率は耐水化処理紙粒重量の約180%であった。
Examples of methods for imparting water resistance to paper particles include a method for vapor-phase formalization, a method for treatment with a fibrous cross-linking agent such as dimethylolethyleneurea, methylolated poly (meth) acrylamide, and polyacrylate. The method of processing etc. are mentioned.
In the method of vapor-phase formalization, dried paper grains are partially formalized with formaldehyde gas in a sealed chamber to give water / chemical resistance and shape memory. The moisture content of the treated paper grain after drying for 2 hours at 105 ° C. × 1 hour at 80% humidity was 7.75% (n: 5), but the untreated paper grain was 9.56%. The reduction in water absorption by this treatment was about 20%. Water-resistant paper grains are completely impregnated with water, placed in a nylon filament mesh bag, stored in a smoke evacuator, and water absorbed for 1 hour at a stacking height of about 30 cm is dropped under the horizontal wire mesh on the pedestal. The water retention after the treatment was about 180% of the weight of the water-resistant paper grain.

ジメチロ−ルエチレン尿素、ポリ(メタ)アクリルアミドのメチロール化物など繊維素架橋剤により処理する方法は、乾いた紙粒を、繊維素架橋剤、例えば純分換算で3.5%のN.N´ジメチロ−ルエチレン尿素などと反応触媒として0.2%の塩化アンモニウムとを含む水溶液に浸漬し、遠心脱水機でピックアップ100%に脱水した後、熱風循環式の乾燥機中で100℃で完全に乾燥した後、更に約130℃で20分間加熱することにより得られる。繊維素架橋剤としては、その他、N.N´ジメチロ−ルアセチレンモノウレイン、N.N´ジメチロ−ルプロピレン尿素等が挙げられる。 In the method of treating with a fibrous cross-linking agent such as dimethylolethyleneurea or methylolated poly (meth) acrylamide, dry paper grains are treated with a fibrous cross-linking agent such as 3.5% N.I. Immerse in an aqueous solution containing N'dimethylolethyleneurea, etc. and 0.2% ammonium chloride as a reaction catalyst, dehydrate to 100% pick-up with a centrifugal dehydrator, and complete at 100 ° C. in a hot air circulating dryer. And dried at about 130 ° C. for 20 minutes. Other examples of the fiber crosslinking agent include N.I. N 'dimethylol acetylene monoureine, N.I. N 'dimethylol propylene urea etc. are mentioned.

本発明に使用する粒状多孔性物質として前記した弾性連続気泡発泡体は、連続気泡の方向を圧縮して通気性を与えた弾性発泡体であり、一方向に通気性を有するという特徴がある。
弾性連続気泡発泡体としては、メラミン/ホルムアルデヒド樹脂製スポンジの圧縮物(以下メラミン樹脂スポンジ接触材という。)等が挙げられる。
メラミン樹脂スポンジ接触材は、スポンジの可撓性や弾性の向上などのため、メラミンの一部分をベンゾグアナミン、アセトグアナミン、スピログアナミンなどのトリアジン誘導体の1種以上で置換して共縮合したもの、その他共縮合可能なもの及び混合物を添加して縮合したものであってもよい。これらの製法や物性に関し下例の他多くの特許文献がある。例えば特開平3−231957号公報、特表平2004−510041号公報、特表平2004−510042号公報等が挙げられる。
The above-mentioned elastic open-cell foam as the granular porous material used in the present invention is an elastic foam that has been given air permeability by compressing the direction of open-cells, and is characterized by air permeability in one direction.
Examples of the elastic open-cell foam include a compressed product of a melamine / formaldehyde resin sponge (hereinafter referred to as a melamine resin sponge contact material).
The melamine resin sponge contact material is a co-condensation product in which a part of melamine is substituted with one or more of triazine derivatives such as benzoguanamine, acetoguanamine, spiroguanamine, etc. in order to improve the flexibility and elasticity of the sponge. What may be condensed and may be condensed by adding a mixture. There are many patent documents other than the following examples regarding these production methods and physical properties. For example, JP-A-3-231957, JP-T-2004-510041, JP-T-2004-510042 and the like can be mentioned.

本発明で使用するメラミン樹脂スポンジ接触材は、通気性が生じるように、メラミン/ホルムアルデヒド樹脂製スポンジを圧縮したものである。
このメラミン/ホルムアルデヒド樹脂製スポンジは、発明者が測定したところ、105℃で1時間乾燥直後の比重が0.0085で相対湿度80±5%で1週間放置した時の比重が0.0096、吸湿率は約11.29%、厚さ4cmであった。
このメラミン樹脂スポンジ接触材は、メラミン/ホルムアルデヒド樹脂製スポンジを下記のように圧縮することにより得ることができる。すなわち、例えば、10cm×10cm×4cm(厚さ)の直方体のスポンジを冷水中に漬けて数回圧縮し、完全に脱気すると水中に沈むが、これを水平な金網に約10分間乗せ、水滴を落下させ含水率が約77%になったものも通気性がほとんどなかった。更にこれを水平に上面から均一に加重し、厚みを3.2cmまで圧縮し、含水率を約60.6%とした場合も通気性は得られなかった。しかし加重を更に増し、厚み、2.7cm以下まで圧縮し、含水率が50%以下となると通気性が増し、本発明の粒状多孔性物質として利用できる可能性を示した。圧縮前のスポンジの厚さが、4cm以上の場合は、厚さがおよそ50%以下になるように、連続気泡の方向に圧縮すると、本発明の目的に合致する通気性が生じるように調節できる。
The melamine resin sponge contact material used in the present invention is obtained by compressing a melamine / formaldehyde resin sponge so that air permeability is generated.
The melamine / formaldehyde resin sponge measured by the inventor has a specific gravity of 0.0085 immediately after drying at 105 ° C. for 1 hour and a specific gravity of 0.0096 when left for 1 week at 80 ± 5% relative humidity. The rate was about 11.29% and the thickness was 4 cm.
This melamine resin sponge contact material can be obtained by compressing a melamine / formaldehyde resin sponge as follows. That is, for example, a 10cm x 10cm x 4cm (thickness) rectangular parallelepiped sponge is immersed in cold water and compressed several times. When completely deaerated, it sinks into water, but it is placed on a horizontal wire mesh for about 10 minutes. Even when the water content was dropped to about 77%, the air permeability was hardly found. Further, even when this was horizontally and uniformly applied from the upper surface, the thickness was compressed to 3.2 cm, and the moisture content was about 60.6%, air permeability was not obtained. However, when the weight was further increased, the thickness was compressed to 2.7 cm or less, and when the water content was 50% or less, the air permeability increased, indicating the possibility of being used as the granular porous material of the present invention. When the thickness of the sponge before compression is 4 cm or more, it can be adjusted so that air permeability meeting the object of the present invention is generated by compressing in the direction of open cells so that the thickness is about 50% or less. .

上記したメラミン樹脂スポンジ接触材等の粒状多孔性物質は、いずれも本発明に使用する気液接触材として有効である。また粒状多孔性物質のうち、例えば配電施設の火災の場合、電線やケ−ブルの火災のように、白煙に随伴するポリ塩化ビニ−ルの熱分解で生じる強刺激性の塩化水素ガスの濃度が高く、粘着性の有害エアロゾルの含有量が比較的少ない場合は、メラミン樹脂スポンジ接触材が最も好ましく、耐水性紙質粒子もこれに匹敵すると考えられる。また住宅やホテルのような火災の煙のように、室内の可燃物の種類が多く、煙エアロゾルとこれに随伴する上記の有害気体の他に合成樹脂類が熱分解で精製する粘着性の有害エアロゾルの濃度が高い場合は、耐水性紙質粒子が最も微細孔の目詰まりによる性能低下が生じ難いと考えられ、最も好ましいものと判断される。
また前記吸湿性化合物として、水酸化ナトリウム、水酸化カリウム等のアルカリ性化合物を用いない場合、吸湿性化合物の水溶液中に、さらにアルカリ金属の水酸化物、重炭酸塩、炭酸塩を含むことが好ましい。アルカリ水溶液を用いることにより、閉鎖空間における火災時に発生する煙エアロゾルと同時に、致死性乃至は強い刺激性有害気体及びエアロゾル(以下有害随伴物という)を解毒することができる。
Any of the above-mentioned granular porous materials such as the melamine resin sponge contact material is effective as the gas-liquid contact material used in the present invention. In addition, among the granular porous materials, for example, in the case of a fire in a distribution facility, there is a strong irritating hydrogen chloride gas generated by thermal decomposition of polyvinyl chloride accompanying white smoke, such as a fire in an electric wire or cable. When the concentration is high and the content of the adhesive harmful aerosol is relatively low, the melamine resin sponge contact material is most preferable, and the water-resistant paper particles are considered to be comparable. There are many types of indoor combustibles, such as fire smoke in houses and hotels. In addition to the smoke aerosol and the harmful gases that accompany it, the synthetic resins can be used to tackify the harmful effects of thermal decomposition. When the concentration of the aerosol is high, it is considered that the water-resistant paper-based particles are most unlikely to deteriorate in performance due to clogging of the fine pores, and are judged to be the most preferable.
Further, when an alkaline compound such as sodium hydroxide or potassium hydroxide is not used as the hygroscopic compound, it is preferable that an aqueous solution of the hygroscopic compound further contains an alkali metal hydroxide, bicarbonate, or carbonate. . By using an alkaline aqueous solution, lethal or strong irritating harmful gases and aerosols (hereinafter referred to as harmful accompanying substances) can be detoxified simultaneously with smoke aerosols generated in a fire in a closed space.

本発明者等は、このことを確認するため、下記(A)〜(C)ような有害随伴物について実験した。この結果、解毒法1〜4のとおり、アルカリ性化合物等を吸湿性化合物水溶液に含ませて煙除去剤として使用すると有害随伴物をも同時に除去できることを確認した。 In order to confirm this, the present inventors conducted experiments on harmful companions such as the following (A) to (C). As a result, as shown in the detoxification methods 1 to 4, it was confirmed that when the alkaline compound or the like was included in the hygroscopic compound aqueous solution and used as a smoke removing agent, harmful accompanying substances could be removed at the same time.

(A)シアン化水素(暴露限界:5ppm)と誘導体(例:アセトンシアノヒドリン:暴露限界4.7ppm)
発生源:発泡ポリウレタン製のクッション材や断熱材、毛織物、絹織物、アクリル繊維、ナイロン繊維類などの燃焼によって生成する。
解毒法1:チオ硫酸塩を加えたアルカリ水溶液を含む煙除去剤を本発明の煙除去装置に使用し、低毒性チオシアネ−ト塩にする。(最良)
解毒法2:pH11程度のアルカリ水溶液で本発明の煙除去装置で洗浄する。
解毒法3:pH11程度のアルカリに次亜塩素酸塩、塩化シアヌル酸塩等酸化剤を加えた液を使用する方法があるが、塩素臭が同伴し排出する欠点があるので1よりも劣る。
(A) Hydrogen cyanide (exposure limit: 5 ppm) and derivatives (example: acetone cyanohydrin: exposure limit 4.7 ppm)
Source: Generated by combustion of foamed polyurethane cushioning material and heat insulating material, woolen fabric, silk fabric, acrylic fiber, nylon fiber, etc.
Detoxification method 1: A smoke removing agent containing an aqueous alkaline solution to which thiosulfate is added is used in the smoke removing apparatus of the present invention to make a low toxicity thiocyanate salt. (best)
Detoxification method 2: Wash with an alkaline aqueous solution of about pH 11 with the smoke removing apparatus of the present invention.
Detoxification method 3: There is a method of using a solution in which an oxidizing agent such as hypochlorite and cyanuric chloride is added to an alkali having a pH of about 11, but it is inferior to 1 because of the disadvantage that chlorine odor is accompanied and discharged.

(B)ハロゲン化水素
フッ化水素(暴露限界:3ppm、眼を強く刺激し消防士や住民の視野を奪う)
発生源:撥水加工衣類の他、フッ素は自然界に広く存在し、生活環境にあるほとんどの
物質に微量付着している。フッ素源から火災時にフッ化水素が必ず生成する。
塩化水素(暴露限界:5ppm)
発生源:電線コードやケーブル、製壁紙などに用いられるポリ塩化ビニール樹脂が火災
熱で生成する。
解毒法4:pH11程度のアルカリ水溶液で本発明の煙除去装置で洗浄する。
(B) Hydrogen halide Hydrogen fluoride (Exposure limit: 3 ppm, strongly irritating eyes and deprives firefighters and residents of visual field)
Source: In addition to water-repellent clothing, fluorine is widely present in nature and is attached to almost all substances in the living environment. Hydrogen fluoride is always generated in the event of a fire from a fluorine source.
Hydrogen chloride (exposure limit: 5 ppm)
Source: Polyvinyl chloride resin used for wire cords, cables, wallpaper, etc. is generated by fire heat.
Detoxification method 4: Wash with an alkaline aqueous solution of about pH 11 with the smoke removing apparatus of the present invention.

(C)毒ガス(煙と混合している場合と毒ガス単独の場合)
サリン、タブン、ソマン、VOxなど神経ガスの解毒に有効とされるアルカリ性水溶液の空間への噴霧法の代わりに、外気との置換率が低い室内の火災あるいは発煙筒による発煙のみの場合は、万一のこれら神経毒ガスの共存を想定して、上記解毒法1の煙除去剤を、本発明の煙除去装置で使用することにより消煙・解毒を達成することができた。
(C) Poisonous gas (if mixed with smoke and poisonous gas alone)
Instead of spraying the alkaline aqueous solution, which is effective for detoxification of nerve gases such as sarin, tabun, soman, VOx, etc., in the case of indoor fire with a low substitution rate with outside air or smoke only by smoke cylinders, Assuming the coexistence of one of these neurotoxin gases, smoke removal and detoxification could be achieved by using the smoke removal agent of the above detoxification method 1 in the smoke removal apparatus of the present invention.

本発明は、閉鎖空間内で、特に火災時に煙エアロゾル等を除去する装置に関するものであり、密閉空間での相対湿度が60%以下であり、常温で飽和濃度の30%以下の濃度の吸湿性化合物水溶液を含有する煙除去剤を含浸させた親水性の粒状多孔性物質からなる気液接触層(A)を備えることを特徴とするものである。
この気液接触層(A)は、前記親水性の粒状多孔性物質を充填した層であり、例えば親水性の粒状多孔性物質をカ−トリッジに収納したもの、ナイロンやポリエステルなどのフィラメント繊維製のメッシュの袋に入れたものが挙げられる。メッシュの袋の場合、1個でもよいし又は複数個を用いてもよい。カートリッジは、粒状多孔性物質を収納した後、その両面から、格子状の押さえと捩子で調節して圧縮できるように調整し、吸気口の上面から、例えば20cm下の定位置にある台座まで挿入・嵌合させる。このカートリッジは、火災時に煙などと共に随伴するシアンガス、塩化水素などの有害随伴物の吸収・解毒に高性能を発揮する本発明の煙除去装置に有効に利用できる。
The present invention relates to an apparatus for removing smoke aerosol or the like in a closed space, particularly in the event of a fire. The relative humidity in the sealed space is 60% or less, and the hygroscopic property has a concentration of 30% or less of the saturated concentration at room temperature. The gas-liquid contact layer (A) comprising a hydrophilic granular porous material impregnated with a smoke removing agent containing an aqueous compound solution is provided.
This gas-liquid contact layer (A) is a layer filled with the hydrophilic granular porous material, for example, a material in which a hydrophilic granular porous material is housed in a cartridge, or made of filament fibers such as nylon or polyester. In a mesh bag. In the case of a mesh bag, one or more may be used. After storing the granular porous material, the cartridge is adjusted so that it can be compressed by adjusting it from both sides with a lattice-shaped presser and screw, and from the upper surface of the intake port to a pedestal at a fixed position, for example, 20 cm below Insert and fit. This cartridge can be effectively used in the smoke removing apparatus of the present invention that exhibits high performance in absorbing and detoxifying harmful accompanying substances such as cyan gas and hydrogen chloride accompanying smoke in a fire.

またこの気液接触層(A)は、煙除去装置の上から所定の高さに設けた台座まで挿入し、気密状に固定するか、装置の吸気口から台座の位置まで収納する。積層する高さは30±5cmがよい。
この装置の材質は、特に限定するものではないが、例えばステンレス、ポリプロピレン、耐水性ハードボード等が挙げられる。
装置の大きさは、特に限定されないが、可搬式の場合は、部屋の入り口の大きさより小さいものであることが必要である。例えば30cm角で、高さが90cmの装置が挙げられる。
The gas-liquid contact layer (A) is inserted from above the smoke removing device to a pedestal provided at a predetermined height, and is fixed in an airtight manner or stored from the air inlet of the device to the position of the pedestal. The stacking height is preferably 30 ± 5 cm.
Although the material of this apparatus is not specifically limited, For example, stainless steel, polypropylene, a water-resistant hard board, etc. are mentioned.
The size of the apparatus is not particularly limited, but in the case of a portable type, it is necessary to be smaller than the size of the entrance of the room. For example, an apparatus having a 30 cm square and a height of 90 cm can be mentioned.

本発明の煙除去装置は、図1のように吸気口(B)から室内の煙と有害随伴物を含む空気を、装置外に設置した吸排気ポンプ(C)で吸引し、本発明の濃厚な煙除去剤水溶液を吸収した親水性、多孔性で通気性のよい気液接触層(A)を通過させて消煙・解毒後に排気する。
吸気口(B)は、円形、楕円形、正方形、矩形他種々の形状が選択できる。例えば粒状多孔性物質をカートリッジに収納する場合は、吸気口の形状にあわせて吸気が漏れないようにすればよい。
前記吸排気ポンプ(C)は、真空ポンプとして用いられるものであれば、いずれのポンプでも使用することができる。またこのポンプは装置内の下部に設置してもよいし、また装置外に設置し装置に結合してもよいが、装置の可搬性などを考慮すると、装置内の外部に設置し、火災時に装置に結合するのが好ましい。ポンプの能力は、密閉空間の広さに応じて適宜選択することができる。
この気液接触層(A)の下の底部には吸湿性化合物水溶液が落下して形成された液溜層(D)がある。液溜層(D)の液面が、気液接触層(A)に接触すると、気流が通過しないため、この液溜層(D)は、分離し、例えば10cm以上離しておく必要がある。
この煙除去装置を可搬式装置として用いる場合は、運転開始時には抱液性の高い該接触材層が既に本発明の濃厚な煙除去剤水溶液を、十分吸収しているため、低容量の閉鎖空間内で、水溶液の補充なしに、かなりの時間、例えば20〜30分間運転することができる。消煙効率が低下した場合は、瓶などに入れた新鮮な液を該接触材層の上から散布すれば、さらに相当時間高度の消煙が可能である。
また大型で定置型の煙除去装置として用いる場合は、液溜層(D)に溜まった煙除去剤をポンプで循環し、気液接触層(A)の上面にノズルから連続的に散布するようにすれば、連続・長時間運転が可能である。
As shown in FIG. 1, the smoke removing apparatus of the present invention sucks air containing indoor smoke and harmful accompanying substances from the air inlet (B) by an intake / exhaust pump (C) installed outside the apparatus, and the rich of the present invention. It passes through a gas-liquid contact layer (A) that has a hydrophilic, porous, and air permeability that absorbs an aqueous smoke remover solution, and is exhausted after smoke removal and detoxification.
As the air inlet (B), various shapes such as a circle, an ellipse, a square, a rectangle and the like can be selected. For example, when a granular porous material is stored in a cartridge, the intake air may be prevented from leaking in accordance with the shape of the intake port.
The intake / exhaust pump (C) can be any pump as long as it is used as a vacuum pump. In addition, this pump may be installed in the lower part of the device, or may be installed outside the device and connected to the device. It is preferably coupled to the device. The capacity of the pump can be appropriately selected according to the size of the sealed space.
There is a liquid reservoir layer (D) formed by dropping the hygroscopic compound aqueous solution at the bottom of the gas-liquid contact layer (A). When the liquid level of the liquid reservoir layer (D) comes into contact with the gas-liquid contact layer (A), the air flow does not pass. Therefore, the liquid reservoir layer (D) needs to be separated, for example, 10 cm or more.
When this smoke removing device is used as a portable device, at the start of operation, the contact material layer having a high liquid-holding property has already sufficiently absorbed the concentrated smoke removing agent aqueous solution of the present invention. Within, it can be run for a considerable time, for example 20-30 minutes, without replenishment of the aqueous solution. When the smoke-dissipating efficiency is lowered, it is possible to extinguish smoke for a considerable time by spraying fresh liquid in a bottle or the like from above the contact material layer.
When used as a large and stationary smoke removal device, the smoke removal agent accumulated in the liquid reservoir (D) is circulated by a pump and continuously sprayed from the nozzle on the upper surface of the gas-liquid contact layer (A). In this way, continuous and long-time operation is possible.

本発明の煙除去装置は、倉庫、旅客機内、事務所、集合住宅、ホテル客室、地下室、料亭、地下室などの小容量の場合は、本発明者らの試験結果から、通風量が30m
/分以下、あるいは通風量10m /分以下の装置でも十分対応できると推定することができる。
これに対し、多層階の地下街、地下鉄駅、遊戯場、映画館、劇場、多層階の集合住宅、百貨店、大容量の倉庫、高層ビル、大型艦船、空港施設、長いトンネルや地下自動車場等で使用する大型で定置式の場合は、例えば30m
/分以上の通風量が必要である。
消防士が視界を失い易く、危険にさらされる狭い閉鎖空間の火災の消煙用には、小型軽量、可搬式、搬送時倒れ難い、液もれが少ない等の設計、大風量で単相電源でも駆動可能などの性能が求められる。また火災時における対応のし易さなどを考慮した仕様が必要となる。
In the case of a small capacity such as a warehouse, passenger aircraft, office, apartment house, hotel room, basement, restaurant, basement, etc., the smoke removal device of the present invention has an air flow rate of 30 m 3 from the test results of the present inventors.
/ Min or less, or it can be estimated that a device with a ventilation rate of 10 m 3 / min or less can sufficiently cope.
On the other hand, in multi-storey underground malls, subway stations, amusement halls, movie theaters, theaters, multi-storey apartments, department stores, large-capacity warehouses, high-rise buildings, large ships, airport facilities, long tunnels and underground car parks, etc. In the case of a large and stationary type to be used, for example, 30 m 3
A ventilation rate of at least / min is required.
Fire extinguisher is easy to lose sight, and it is designed to be small, lightweight, portable, difficult to collapse during transportation, and with little air leaks, for single-phase power supply with a large air volume, for extinguishing fires in confined spaces But any performance that can be driven is required. Also, specifications that take into account the ease of handling in the event of a fire are required.

以下、本発明を実施例によりさらに具体的に説明する。
まず本発明の実施例に使用する、発煙室、発煙方法、煙除去剤、煙除去装置、相対湿度の測定方法及び評価法について説明する。
1.発煙室
1.8m×1.8mの地盤に深さ0.3mの穴を掘り、ここにコンクリートを水平に打設し、地下水の浸入を遮断した土台の4隅に杭を打ち込み、この杭に高さ1.8mで38mm×90mmの材木の柱を固定し、同じ材木を4本の梁で4分割した位置にこれら柱を水平につなぐ直方体の躯体を固定した。コンクリートの底面から0.35mの位置の床板と天井板9プライの耐水性ラワン合板を張り、更に天井の上には、雨水を流すためポリカーボネート製の波板で片屋根を作り設置した。床面より下部の側面は、床板と同じ合板を4面に張り、降雨と強風を遮断した。正面の0.9m幅と3面に1mm厚のポリエチレンフィルムを、2mm厚の薄板でネジ止めで固定し、正面の0.9m幅の部分に、その外側に蝶番(ちょうつがい)を用いて外側にのみ開く戸(開き戸)を取り付けた。さらにその開き戸の裏側との隙間を少なくし気密性を向上するため、該戸の左右に床板と同じ合板で、幅0.1mの板を支柱として取り付け、該開き戸の上から0.3mに開閉可能な外気取り入れ口と、この下から32cmの位置に排気用アルミニウム製の直径0.3mフレキシブルパイプ挿入口を開口し、間隙は濡れタオルを巻きつけ漏洩を防止する方式で行い、内容量約4.7mの直方体の空間を有する発煙室を作製した。
Hereinafter, the present invention will be described more specifically with reference to examples.
First, a smoke generation chamber, a smoke generation method, a smoke removal agent, a smoke removal device, a relative humidity measurement method and an evaluation method used in the examples of the present invention will be described.
1. Smoke chamber A hole with a depth of 0.3m is dug in the ground of 1.8m x 1.8m, concrete is laid horizontally here, and piles are driven into the four corners of the foundation where the infiltration of groundwater is blocked. A timber pillar with a height of 1.8 m and 38 mm × 90 mm was fixed, and a rectangular parallelepiped box was fixed at a position where the same timber was divided into four beams by four beams. A floorboard 0.35m from the bottom of the concrete and a 9-ply water-resistant lauan plywood were stretched, and a roof was made on the ceiling with a corrugated sheet made of polycarbonate to allow rainwater to flow. On the side of the floor below the floor, the same plywood as the floorboard was placed on four sides to block rain and strong winds. The front 0.9m width and 1mm thick polyethylene film on 3 sides are fixed with a 2mm thin plate with screws, and the front 0.9m wide part is hinged outside. A door that opens only to the door (a hinged door) was attached. Furthermore, in order to reduce the gap with the back side of the hinged door and improve the airtightness, the same plywood as the floorboard is attached to the left and right of the door, and a 0.1m wide plate is attached as a column, and it opens and closes from the top of the hinged door to 0.3m An open air inlet with a diameter of 0.3 m and a flexible pipe insertion port made of aluminum for exhaust is opened at a position 32 cm from the bottom. A smoke chamber having a rectangular parallelepiped space of 7 m 3 was produced.

2.発煙方法
(株)ケイアンドケイ製の発煙筒(Smoke BOMB)を用いた発煙方法、発煙筒を用いずに白煙及び黒鉛を発生させる方法について説明する。
<発煙筒>
6塩化エタン、酸化亜鉛、亜鉛の配合物が約8割程度封入され、発煙量約100mと公表されている径53mm、高さ6mmの円筒形の缶を使用直前に開缶し、発煙室内でマッチで着火し、開き戸を閉じて煙を充満させた。
<白煙>
内径24cm、深さ6cmの平底のステンレス製の鍋に、太さ1mmの銅線3本をそれぞれ直径20cmの円形に成型して鍋底に積み上げ、その上面が該鍋より2cm高い位置になるように設置した架台に、0.2mm径のステンレス製金網をかぶせた。この金網上に木粉とポリエチレンの等量を加熱溶融し射出成型した(平均23.5個/g)のペレット40gに灯油7gを均一に混合し、均一に隙間のないように並べた後、幅約2cmのティッシュペーパーをペレットの上に乗せ、ライターで着火し、該ペレット全体が黒くなるまで約2分間、発煙燃焼させ、鍋に約1分間蓋をして、発煙燃焼が継続している場合は、更に蓋をして炎が消え、白煙が盛んに発生していることを確認した後、発煙室に入れ、開き戸を閉じ、白煙発生が停止した後で消煙試験を行った。
2. Smoke generation method A smoke generation method using a smoke cylinder (Smoke BOMB) manufactured by K & K Corporation, and a method of generating white smoke and graphite without using the smoke cylinder will be described.
<Smoke tube>
About 80% of a mixture of ethane hexachloride, zinc oxide, and zinc is sealed, and a cylindrical can with a diameter of 53 mm and a height of 6 mm, which is announced as a smoke generation amount of about 100 m 3 , is opened just before use. Ignited with a match, closed the hinged door and filled with smoke.
<White smoke>
In a flat-bottomed stainless steel pan with an inner diameter of 24 cm and a depth of 6 cm, three copper wires with a thickness of 1 mm are each molded into a circle with a diameter of 20 cm and stacked on the bottom of the pan so that the top surface is 2 cm higher than the pan. A stainless steel wire mesh having a diameter of 0.2 mm was placed on the installed base. 7 g of kerosene was uniformly mixed with 40 g of pellets obtained by heating, melting and injection-molding (equal 23.5 pcs / g) of equal amounts of wood powder and polyethylene on this wire mesh, and arranged uniformly without gaps. Place a tissue paper with a width of about 2cm on the pellet, ignite with a lighter, smoke and burn for about 2 minutes until the whole pellet turns black, cover the pan for about 1 minute, and smoke combustion continues In this case, the lid was further covered and the flame disappeared, and it was confirmed that white smoke was actively generated. Then, it was placed in the smoke chamber, the hinged door was closed, and the smoke generation test was conducted after the generation of white smoke stopped. .

<黒煙>
1)前記白煙の発生において、ポリエチレンの代わりに、芳香族のポリカーボネートを使用したペレットを使用して同様に発煙させて、消煙試験を行った。この場合分散性のよい黒煙が得られた。
2)断熱性の皿の上に缶詰の空き缶に20〜40mlのトルエンまたはスチレンを発煙室に入れ、ライターで着火し、開き戸を閉じ、燃え尽きるまで発煙させた後、消煙試験を行った。この場合煙エアロゾルが時間の経過とともに糸状に凝集した黒煙が生じる傾向があったが、燃焼持続には室外から新鮮空気の補給が必要な場合があり、その量にもよるが、発煙室内の視界が回復するまでに6〜12時間を要した。
<Black smoke>
1) In the generation of the white smoke, smoke was tested in the same manner by using pellets using aromatic polycarbonate instead of polyethylene. In this case, black smoke with good dispersibility was obtained.
2) 20-40 ml of toluene or styrene was put in a canned empty can on a heat-insulating dish, ignited with a lighter, closed on the open door, and smoked until it was burned out, and then a smoke extinction test was conducted. In this case, there was a tendency for the smoke aerosol to form agglomerated black smoke over time, but it may be necessary to replenish fresh air from outside the room in order to sustain combustion. It took 6-12 hours for the visibility to recover.

3.煙除去剤
(a)酢酸カリウム[20℃での相対湿度(以下RHという。) 20%、168℃でのRH 13%]
CHCOOK Mw:98.15、白色粉末、mp:292℃、Sp.Gr.:1.8、LD50:3250mg/Kg(ラット)、水に対する溶解度:217g/100g、何らかの原因で粉塵爆発性があるが、臭化アンモニウムの水溶液への混合で爆発を防止することができる。(相溶性試験未了)
消煙処方:CHCOOK/水=70g/30g
<消煙性があり、低毒性、環境に放流した場合汚染が少ないとみなされる物質>
(b)塩化マグネシウム・6水塩(5〜45℃でのRH 33%)
Mgcl・6HO Mw:203.33、水に対する溶解度:35.14g/100g(20℃)、無水物なし
加熱により200℃でHClを発生し、オキシ塩化物となり、約600℃でMgO(マグネシア)を生成する。
(c)塩化カルシウム(無水物、1,2,4及び6水塩あるが、水溶液を使用するため6水塩を使用する。)
CaCl・6HO Mw:219.06、水に対する溶解度:29.5g/100g(20℃)、15〜25℃での飽和水溶液のRH 29%)
3. Smoke removing agent (a) Potassium acetate [relative humidity at 20 ° C. (hereinafter referred to as RH) 20%, RH 13% at 168 ° C.]
CH 3 COOK Mw: 98.15, white powder, mp: 292 ° C., Sp. Gr. : 1.8, LD 50 : 3250 mg / Kg (rat), solubility in water: 217 g / 100 g, dust explosive for some reason, but mixing with an aqueous solution of ammonium bromide can prevent explosion. (Compatibility test incomplete)
Smoke-free formulation: CH 3 COOK / water = 70 g / 30 g
<Substances that are smoke-free, have low toxicity, and are considered to be less pollutant when released to the environment>
(B) Magnesium chloride hexahydrate (RH 33% at 5-45 ° C.)
Mgcl 2 · 6H 2 O Mw: 203.33, solubility in water: 35.14 g / 100 g (20 ° C.), generation of HCl at 200 ° C. by heating without anhydride to form oxychloride, and MgO ( Magnesia).
(C) Calcium chloride (anhydrous, 1, 2, 4 and hexahydrate, but hexahydrate is used since an aqueous solution is used.)
CaCl 2 · 6H 2 O Mw: 219.06, solubility in water: 29.5 g / 100 g (20 ° C.), RH 29% of saturated aqueous solution at 15-25 ° C.)

<消煙性は優れるが、毒性、刺激性、環境に放流した場合汚染の問題があると考えられる物質>
(d)燐酸(HPO・1/2HO、92.25%) 24.5℃でのRH 9%
(e)塩化リチウム・1水塩(LiCl・1HO、20〜65℃でのRH 11%)
(f)臭化カルシウム・6水塩(CaBr・6HO Mw:199.89、11〜22℃のRH 16%)
(g)臭化亜鉛(ZnBr Mw:225.20、水に対する溶解度:394g/100g 飽和水溶液:80% 5〜30℃でのRH 8%)
(h)水酸化ナトリウム(NaOH・HO、15〜60℃でのRH 6%)
(i)水酸化カリウム(KOH・2HO、5〜30℃でのRH 9%)
(j)その他種々の潮解性の塩類が挙げられる。
<Substances with excellent smoke-extinguishing properties, but are considered toxic, irritating and contaminated when released to the environment>
(D) phosphoric acid (H 3 PO 4 · 1 / 2H 2 O, 92.25%) 24.5 9% RH at ℃
(E) Lithium chloride monohydrate (LiCl · 1H 2 O, RH 11% at 20 to 65 ° C.)
(F) calcium bromide hexahydrate (CaBr 2 · 6H 2 O Mw : 199.89,11~22 16% RH in ° C.)
(G) Zinc bromide (ZnBr 2 Mw: 225.20, solubility in water: 394 g / 100 g saturated aqueous solution: 80% RH 8% at 5-30 ° C.)
(H) Sodium hydroxide (NaOH.H 2 O, RH 6% at 15 to 60 ° C.)
(I) Potassium hydroxide (KOH · 2H 2 O, RH 9% at 5 to 30 ° C.)
(J) Other various deliquescent salts can be mentioned.

4.相対湿度の測定方法
RHは、水蒸気圧と飽和水蒸気圧との比を%で表わしたものである。一般的に種々の測定方法が採用されている。これらの方法により値が10〜20%も変動する場合が多いが、本発明の実験では、種々比較検討の結果、静電容量式湿度センサーを用いた日本カノマックス製クリモマスターMODEL6531を用いた。消煙効果が優れ、強い毒性や刺激性がなく、環境への負荷も少ない前記吸湿性化合物の選択に、これらが存在する密閉空間のRHの測定を行って選定し、毒性や刺激性も少なく最も好ましい吸湿性化合物として、下記(イ)〜(ハ)を選んだ。これらの気流の測定では、それぞれ数十秒で安定したRH指示値を示した。
静止空間の場合は、10分以上も要する場合もあったため、プローブの先端を動かすと数分間で安定した指示値を示した。このような方法でRHは正当に測定できているものと判断した。
(イ)無水塩化カルシウムを入れた1Lの密閉容器空間は、いずれも25℃でのRHが3.2%で、同様の方法で過飽和の無水塩化カルシウムが62.5%、55.6%及び50%の水溶液の25℃でのRHがそれぞれ、24.1%、39.2%であった。
(ロ)(イ)と同様の条件で、酢酸カリウムの飽和水溶液を入れた密閉空間がいずれも25℃の場合のRHは、24.4、60%水溶液の場合のRHは44.1%、濃度が50%水溶液の場合のRHは56.1%であった。
(ハ)塩化マグネシウム6水塩のみを加えた密閉空間の25℃でのRHは34.0%、41.0%、飽和水溶液の場合のRH42.9%であった。
4). Method for Measuring Relative Humidity RH is the ratio of water vapor pressure to saturated water vapor pressure expressed in%. In general, various measurement methods are employed. Although these values often vary by 10 to 20% by these methods, in the experiments of the present invention, as a result of various comparative studies, Kurimo Master MODEL6531 manufactured by Nippon Kanomax was used. Select the hygroscopic compounds with excellent smoke-fusing effect, strong toxicity and irritation, and less environmental burden by measuring the RH of the enclosed space where they exist, with less toxicity and irritation The following (i) to (c) were selected as the most preferred hygroscopic compounds. In the measurement of these airflows, stable RH indication values were shown in several tens of seconds.
In the case of a static space, it may take 10 minutes or more, so when the tip of the probe is moved, a stable indicated value is displayed within a few minutes. It was judged that RH could be properly measured by such a method.
(I) 1 L sealed container space containing anhydrous calcium chloride has 3.2% RH at 25 ° C., and 62.5%, 55.6% supersaturated anhydrous calcium chloride in the same manner, and The RH at 25 ° C. of the 50% aqueous solution was 24.1% and 39.2%, respectively.
(B) Under the same conditions as in (a), when the sealed space containing a saturated aqueous solution of potassium acetate is 25 ° C., the RH is 24.4, when the 60% aqueous solution is 44.1%, In the case of a 50% aqueous solution, the RH was 56.1%.
(C) The RH at 25 ° C. of the sealed space to which only magnesium chloride hexahydrate was added was 34.0%, 41.0%, and RH 42.9% in the case of a saturated aqueous solution.

(比較例1)
発煙室内を密閉状態に保ち、発煙筒で煙を充満させて放置した場合は、発煙室の1面から反対面への見通しが可能となるになるまでに6時間以上を要し、12時間後もかなりの白煙が残留した。
(Comparative Example 1)
If the smoke chamber is kept sealed and smoke is filled with a smoke cylinder, it will take more than 6 hours to see from one side of the smoke chamber to the other side, and 12 hours later Even considerable white smoke remained.

(比較例2)
耐水処理を施した本発明の紙粒をナイロンフィラメント繊維製の網状の袋に入れてから、水槽に浸漬して空気を完全に追い出し、本発明の煙除去装置吸気口内に設けた台座の上に水平に固定した金属の格子上に約30cmの高さに隙間のないように収納し、紙粒に吸収されなかった余分の水が装置内の底部の溶液槽に滴下し終わった後、発煙室の開き戸の開口に径20cmのアルミニウムフレキシブルパイプ(以下、フレキという。)の一端を気密状に挿入して装置内に入れ、装置外の送風ポンプの吸気口に連結し、その排気口に3mの同径のフレキを連結した。送風ポンプに、製造会社定格の単相100V、出力0.4Kw、50Hz、回転数2870rpm、最大風量13m /分、最大静圧95mmAqを配線し、発煙室の開き戸を開け、予備試験により、送風機の運転による大きな負圧によって発煙室側面に取り付けたポリエチレンフィルムが破損・脱落しないように調節した。ついで、開き戸を開け、発煙筒に着火して発煙室内に置き、速やかに開き戸を閉じた、該発煙筒は約3〜4秒間で燃え尽き、白煙は発煙室内に充満した後、発煙室の1面から1.8m離れた反対面への視界は完全に失われた。そこで、送風ポンプを駆動させたところ、ほとんど消煙されないまま、該送風ポンプ排気口から刺激性のある白煙が吐出し、無風の晴天下のため発煙室周辺に高濃度の白煙が立ちこめ、発煙室は保存林に近接する場所であったため、火災と誤認される恐れがあった。30秒後に送風ポンプを停止させたが、発煙室内は反対面がなんとか見渡せる程度まで回復した。そこで、開き戸を少し開けたままにして自然排気により完全に排煙させた。
(Comparative Example 2)
Put the water-resistant paper grain of the present invention in a mesh bag made of nylon filament fiber, and then immerse it in a water tank to completely expel the air, on the pedestal provided in the air inlet of the smoke removal apparatus of the present invention It is stored on a horizontally fixed metal grid so that there is no gap at a height of about 30 cm, and after the excess water that has not been absorbed by the paper grains has been dripped into the solution tank at the bottom of the device, the smoke chamber One end of an aluminum flexible pipe (hereinafter referred to as “flexible”) having a diameter of 20 cm is inserted into the device in an airtight manner into the opening of the hinged door, and is connected to the intake port of the blower pump outside the device. Flexible cables with the same diameter were connected. The manufacturer's rated single-phase 100V, output 0.4Kw, 50Hz, rotation speed 2870rpm, maximum air volume 13m 3 / min, maximum static pressure 95mmAq, open the smoke door and open the blower The polyethylene film attached to the side of the smoke chamber was adjusted so that it was not damaged or dropped by the large negative pressure generated during the operation. Next, the hinged door was opened, the smoke cylinder was ignited and placed in the smoke chamber, and the hinged door was quickly closed. The smoke cylinder burned out in about 3 to 4 seconds, and white smoke filled the smoke chamber. Visibility to the opposite surface 1.8m away from the surface was completely lost. Therefore, when the blower pump was driven, irritating white smoke was discharged from the blower pump exhaust port with almost no smoke extinguished, and high-concentration white smoke stood up around the smoke generation chamber because of no wind in fine weather, The smoke chamber was close to the conservation forest and could be mistaken for a fire. After 30 seconds, the blower pump was stopped, but the inside of the smoke chamber recovered to the extent that the other side could be seen. Therefore, we left the hinged door a little open and exhausted it completely by natural exhaust.

(実施例1)
水の代わりに酢酸カリウムの飽和水溶液を使用する以外は、比較例2と同じ試験を行った。送風ポンプを駆動させたところ、完全に消煙され、刺激性のない透明な空気が排出され、発煙室の周辺には全く煙が漂よわず、30秒後には発煙室の側面から反対面がなんとか見渡せる程度まで回復し、1分後には反対面が見渡せる程度まで回復し、2分後には完全に発煙室内は透明になった。
(Example 1)
The same test as Comparative Example 2 was performed except that a saturated aqueous solution of potassium acetate was used instead of water. When the blower pump is driven, smoke is completely extinguished, transparent air that is not irritating is exhausted, no smoke drifts around the smoke chamber, and after 30 seconds, the opposite surface is seen from the side of the smoke chamber. It recovered to some extent, and after 1 minute it recovered to the other side, and after 2 minutes the smoke chamber was completely transparent.

(実施例2)
開き戸の開口から耐水性電源コ−ドを気密状に入れ、送風ポンプに連結して、発煙室に持ち込み、空気取り入れ口を閉じ、比較例2と同様に発煙室内に白煙を充満させてから送風ポンプを駆動させた。30秒後には、発煙室内の白煙は、反対面が見通せる程度まで視界が回復し、2分30秒後にはほぼ発煙室内は透明になり、発煙室の周囲には白煙の滞留を認めなかった。
(Example 2)
Put the water-resistant power cord in an airtight manner from the opening of the hinged door, connect it to the blower pump, bring it into the smoke chamber, close the air intake, and fill the smoke chamber with white smoke as in Comparative Example 2. The blower pump was driven. After 30 seconds, the white smoke in the smoke chamber recovered to the extent that the other side could be seen, and after 2 minutes and 30 seconds, the smoke chamber became almost transparent, and no white smoke was found around the smoke chamber. It was.

(実施例3)
開き戸の開口から耐水性コ−ドのみを気密状に入れ、送風ポンプに連結して、発煙室に持ち込み、空気取り入れ口を閉じ、上記の木粉とポリエチレンの混融ペレットの炎を伴わない(くすぶり)燻焼による白煙を充満せて、実施例1と同様に送風ポンプを駆動させた。30秒後には、発煙室内の白煙は、反対面が見渡せる程度まで視界が回復し、2分30秒後にはほぼ発煙室内は透明になり、その周囲にも白煙の滞留を認めなかった。
(Example 3)
Only the water-resistant cord is put in an airtight manner through the opening of the hinged door, connected to the blower pump, brought into the smoke generation chamber, the air intake port is closed, and the flame of the mixed powder pellet of wood powder and polyethylene is not accompanied ( Smoldering) White smoke from smoldering was filled, and the blower pump was driven in the same manner as in Example 1. After 30 seconds, the visibility of white smoke in the smoke chamber was restored to the extent that the opposite surface could be seen, and after 2 minutes and 30 seconds, the smoke chamber became almost transparent, and no white smoke remained in the surrounding area.

(実施例4)
煙除去装置の吸気口内部の台座の位置に、厚さが4cmで、その方向が通気方向である連続気泡体を形成しているメラミン/ホルムアルデヒド樹脂を基材とする親水性弾性連続気泡発泡体(略称:メラミン樹脂スポンジ)のスラブを装置の内部の台座による定位置まで隙間なく、通気性を向上するため厚さを圧縮して収納できるカ−トリッジを気液接触材とした。該カ−トリッジは、3cm角の木材の枠の下面に、開孔率約50%で厚さ約3mmで、木質繊維をフェノ−ル樹脂で固着したハ−ドボ−ド製の耐水性板で、該木枠に水平に固定し、該耐水性板を木枠の内側約2cmの各中央部に径1cmのボ−ルドとナットで垂直に固定し、更に該木枠の内部に該スラブを気流の方向に密着して並べ、その上にステンレス製金網を置き、更に木枠の内部と同形で密着して挿入できる該耐水性板を上面とし、該ボ−ルドが垂直に貫通するよう同径に開孔し、上部のナットを締めてスラブの厚さが約2cmなるように圧縮した後、塩化カルシウムの飽和水溶液に浸漬して、完全に吸収させてから比較例2と同じ方法で消煙試験を行い、約30秒後には、消煙室の内部の白煙は、反対面が見渡せる程度まで視界が回復し、2分30秒後には発煙室内は透明になり、発煙室の周囲には白煙の滞留を認めなかった。
Example 4
Hydrophilic elastic open-cell foam based on melamine / formaldehyde resin forming an open-cell body with a thickness of 4 cm and a direction of ventilation at the position of the pedestal inside the air inlet of the smoke removal device A gas-liquid contact material was used as a cartridge that can accommodate a slab of (abbreviation: melamine resin sponge) without compressing the slab to a fixed position by a pedestal inside the apparatus and compressing the thickness in order to improve air permeability. The cartridge is a hard board made of hardboard having a hole area of about 50%, a thickness of about 3 mm, and a wood fiber fixed with phenolic resin on the lower surface of a 3 cm square wood frame. The water-resistant plate is fixed horizontally to the center of each 2 cm inside the wooden frame with a 1 cm diameter ball and nut, and the slab is further fixed inside the wooden frame. Place in close contact with the direction of the air flow, place a stainless steel wire mesh on it, and use the water-resistant plate that can be inserted in close contact with the inside of the wooden frame as the top surface. After the hole was opened to the diameter, the upper nut was tightened and the slab was compressed so that the thickness of the slab was about 2 cm, immersed in a saturated aqueous solution of calcium chloride, completely absorbed, and then erased in the same manner as in Comparative Example 2. A smoke test was conducted, and after about 30 seconds, the white smoke inside the smoke evacuation chamber was reduced to the extent that the opposite side could be seen. And, after 2 minutes and 30 seconds fuming room becomes transparent, around the fuming chamber was no retention of white smoke.

(実施例5)
実施例3の方法で発煙室に白煙を充満させる以外は、実施例4と同じ試験を行った。送風ポンプ駆動35秒後には、消煙室の内部の白煙は反対面が見渡せる程度まで視界が回復し、2分30秒後には発煙室内は透明になり、発煙室の周囲には白煙の滞留を認めなかった。
(実施例6)
塩化マグネシウムの過飽和溶液を使用する以外は実施例5と同じ試験を行った。送風ポンプ駆動35秒後には、消煙室の内部の白煙は反対面が見渡せる程度まで視界が回復し、2分45秒後には発煙室内は透明になり、発煙室の周囲には白煙の滞留を認めなかった。
(Example 5)
The same test as in Example 4 was performed, except that the smoke chamber was filled with white smoke by the method of Example 3. After 35 seconds of driving the blower pump, the white smoke inside the smoke evacuation chamber is restored to the extent that the opposite side can be seen, and after 2 minutes and 30 seconds the smoke chamber becomes transparent, and there is white smoke around the smoke chamber. No stagnation was observed.
(Example 6)
The same test as in Example 5 was performed except that a supersaturated solution of magnesium chloride was used. After 35 seconds, the white smoke inside the smoke evacuation chamber is restored to the extent that the opposite side can be seen. After 2 minutes and 45 seconds, the smoke chamber becomes transparent, and there is white smoke around the smoke chamber. No stagnation was observed.

(実施例7)
比較例2と同様の方法で、耐水化紙粒の代わり粒状活性炭を、水の代りに酢酸カリウムの飽和水溶液99.5重量%に45%の水酸化カリウム水溶液0.5%の混合液を吸収させてから消煙器内に収納し、前記のとおり発生させた黒煙1)を発煙室に充満させ、実施例2と同じ方法で送風ポンプを駆動した。発煙室外に排出される空気は、黒煙やこの凝集物を含まず、実施例6と同様、発煙室内の視界も急速に回復した。
(実施例8)
発煙方法が、発煙室内で20mlのトルエンと5gのポリウレタンとを同時に燃焼させて前記の黒煙2)を発生させた以外は、実施例7と同じ消煙試験を実施した。発煙室外に排出される空気は、黒煙とこの凝集物を含まなかったが、発煙室側面のポリエチレンフィルムと木質部分全面にすすの微粒子が微量付着したため、正確な視野回復時間の測定が遅れたが、約1分後には発煙室の1面から反対面までの視野は回復した。また送風ポンプ駆動直後の排気のシアン化水素濃度を北川式ガス検知管(光明理化学工業製の検知管112SB、測定範囲:0.5〜100ppm)で測定したが、検出されなかった。
(Example 7)
In the same manner as in Comparative Example 2, granular activated carbon was absorbed instead of water-resistant paper particles, and a mixed solution of 45% potassium hydroxide aqueous solution 0.5% in 99.5% by weight saturated aqueous potassium acetate solution instead of water. Then, it was stored in a smoke eliminator and the black smoke 1) generated as described above was filled in the smoke generation chamber, and the blower pump was driven in the same manner as in Example 2. The air discharged to the outside of the smoke generation chamber does not contain black smoke or this agglomerate, and the field of view inside the smoke generation chamber recovered rapidly as in Example 6.
(Example 8)
Except for the smoke generation method, 20 ml of toluene and 5 g of polyurethane were simultaneously burned in the smoke generation chamber to generate the black smoke 2), and the same smoke extinction test as in Example 7 was performed. The air discharged outside the smoke chamber did not contain black smoke and this agglomerate, but because of a small amount of fine particles of soot adhering to the entire polyethylene film and the wood part on the side of the smoke chamber, accurate visual field recovery time measurement was delayed. However, the field of view from one side of the smoke chamber to the opposite side recovered after about 1 minute. Moreover, although the hydrogen cyanide density | concentration of the exhaust_gas | exhaustion immediately after a blast pump drive was measured with the Kitagawa type | formula gas detector tube (detector tube 112SB made from Komeiri Chemical Industry, measurement range: 0.5-100 ppm), it was not detected.

本発明の煙エアロゾル除去装置の側面図を表す。The side view of the smoke aerosol removal apparatus of this invention is represented.

符号の説明Explanation of symbols

1:汚染気体の入口
2:気液接触層
3:清浄気体の出口
4、4’:邪魔板
5:液溜層
6:ドレイン出口
1: Contaminated gas inlet 2: Gas-liquid contact layer 3: Clean gas outlet 4, 4 ': Baffle plate 5: Reservoir layer 6: Drain outlet

Claims (8)

密閉空間での相対湿度が60%以下であり、常温で飽和又は飽和濃度の30%以上の濃度の吸湿性化合物水溶液を含有することを特徴とする閉鎖空間内の煙エアロゾル除去剤。 A smoke aerosol removal agent in a closed space, comprising a hygroscopic compound aqueous solution having a relative humidity in a sealed space of 60% or less and a saturation or a saturation concentration of 30% or more at normal temperature. 前記吸湿性化合物が、酢酸カリウム、塩化カルシウム及び塩化マグネシウムからなる群から選ばれる1種以上である請求項1記載の閉鎖空間内の煙エアロゾル除去剤。 The smoke aerosol removing agent in a closed space according to claim 1, wherein the hygroscopic compound is at least one selected from the group consisting of potassium acetate, calcium chloride and magnesium chloride. 前記吸湿性化合物がアルカリ性化合物でない場合、さらにアルカリ性化合物を含む請求項1又は2記載の閉鎖空間内の煙エアロゾル除去剤。 The smoke aerosol removal agent in a closed space according to claim 1 or 2, further comprising an alkaline compound when the hygroscopic compound is not an alkaline compound. 密閉空間での相対湿度が60%以下であり、常温で飽和濃度の30%以下の濃度の吸湿性化合物水溶液を含有する煙エアロゾル除去剤を含浸させた親水性の粒状多孔性物質からなる気液接触層(A)を備えることを特徴とする閉鎖空間内の煙エアロゾル除去装置。 A gas-liquid comprising a hydrophilic granular porous material impregnated with a smoke aerosol removing agent containing a hygroscopic compound aqueous solution having a relative humidity of 60% or less and a saturation concentration of 30% or less at normal temperature in a sealed space. A device for removing smoke aerosol in a closed space, comprising a contact layer (A). 前記粒状多孔性物質が、耐水性紙質粒子、親水性の弾性連続気泡発泡体、親水性の吸水性活性炭、吸水性セラミックのいずれかである請求項4記載の閉鎖空間内の煙エアロゾル除去装置。 The smoke aerosol removal device in a closed space according to claim 4, wherein the particulate porous material is any one of water-resistant paper particles, hydrophilic elastic open-cell foam, hydrophilic water-absorbing activated carbon, and water-absorbing ceramic. 前記親水性の弾性連続気泡発泡体が、分子中にトリアジン環を有する化合物とホルムアルデヒドとを共縮合させて得られるアミノ樹脂の発泡体である請求項5記載の閉鎖空間内の煙エアロゾル除去装置。 6. The smoke aerosol removal apparatus in a closed space according to claim 5, wherein the hydrophilic elastic open-cell foam is an amino resin foam obtained by co-condensing a compound having a triazine ring in a molecule and formaldehyde. 前記気液接触層(A)が、前記煙エアロゾル除去剤を含浸させた親水性の多孔性物質をケース内に収納したカートリッジからなるか、又は前記多孔性物質を入れたメッシュの袋からなる請求項4〜6のいずれか1項に記載の閉鎖空間内の煙エアロゾル除去装置。 The gas-liquid contact layer (A) comprises a cartridge containing a hydrophilic porous material impregnated with the smoke aerosol removing agent in a case, or a mesh bag containing the porous material. Item 7. The smoke aerosol removing device in the enclosed space according to any one of Items 4 to 6. 密閉空間での相対湿度が60%以下であり、常温で飽和濃度の30%以下の濃度の吸湿性化合物水溶液を含有する煙エアロゾルの除去剤を含浸させた親水性の粒状多孔性物質からなる気液接触層(A)を備え、その上部に空気の吸気口(B)を備え、前記気液接触層(A)の下部に10cm以上分離して液溜層(D)を備えたエアロゾル除去装置に、前記装置外に設置した吸排気ポンプ(C)を結合し、前記吸排気ポンプ(C)により煙エアロゾルを含む空気を吸気口(B)から吸入し、前記気液接触層(A)に接触通過させることを特徴とする、閉鎖空間内の煙エアロゾルを除去する方法。

A gas composed of a hydrophilic granular porous material impregnated with a smoke aerosol remover containing a hygroscopic compound aqueous solution having a relative humidity of 60% or less and a saturation concentration of 30% or less at normal temperature in a sealed space. An aerosol removing device comprising a liquid contact layer (A), an air inlet (B) at the top, and a liquid reservoir layer (D) separated by 10 cm or more below the gas-liquid contact layer (A) And an intake / exhaust pump (C) installed outside the apparatus, and the intake / exhaust pump (C) sucks air containing smoke aerosol from the intake port (B), and enters the gas-liquid contact layer (A). A method for removing smoke aerosol in a confined space, characterized by passing through contact.

JP2007262303A 2007-10-05 2007-10-05 Scavenger of smoke aerosol in enclosed space, its apparatus and method for scavenging smoke aerosol in closed space using its apparatus Pending JP2009090194A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102032994A (en) * 2010-12-22 2011-04-27 中国科学技术大学 Subway carriage fire experiment table
CN102750848A (en) * 2012-06-08 2012-10-24 中国科学技术大学 Subway station fire experiment simulation device
CN107854923A (en) * 2017-11-29 2018-03-30 安徽未名科键环境有限公司 A kind of flue gas white-smoke-removing device
CN107894255A (en) * 2017-11-17 2018-04-10 国网浙江省电力公司 A kind of power distribution network running environment monitoring device

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102032994A (en) * 2010-12-22 2011-04-27 中国科学技术大学 Subway carriage fire experiment table
CN102750848A (en) * 2012-06-08 2012-10-24 中国科学技术大学 Subway station fire experiment simulation device
CN107894255A (en) * 2017-11-17 2018-04-10 国网浙江省电力公司 A kind of power distribution network running environment monitoring device
CN107854923A (en) * 2017-11-29 2018-03-30 安徽未名科键环境有限公司 A kind of flue gas white-smoke-removing device

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