JP2005074333A - Exhaust gas treatment apparatus - Google Patents

Exhaust gas treatment apparatus Download PDF

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JP2005074333A
JP2005074333A JP2003309014A JP2003309014A JP2005074333A JP 2005074333 A JP2005074333 A JP 2005074333A JP 2003309014 A JP2003309014 A JP 2003309014A JP 2003309014 A JP2003309014 A JP 2003309014A JP 2005074333 A JP2005074333 A JP 2005074333A
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exhaust gas
activated carbon
treatment apparatus
powder
gas treatment
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Hiroshi Akutagawa
宏 芥川
Hidekazu Oshita
英一 大下
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Panasonic Holdings Corp
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Matsushita Electric Industrial Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide an exhaust gas treatment apparatus based on a dry treatment of the burning exhaust gas of synthetic resin products and ensuring control of the emission of dioxins, dust and smelling ingredients below specified values. <P>SOLUTION: The apparatus is for treatment of 200°C or lower exhaust gas emitted from the combustion chamber burning synthetic resin products and has a treating powder supplying section 22 spraying and supplying a mixed powder of activated carbon and slaked lime into the gas, a bag filter 24 removing powder from the gas and an activated carbon adsorption section which consists of an activated carbon layer 27a for neutrality arranged in the first half and composed of ordinary carbon and an activated carbon layer 27b for acid arranged in the second half and composed of a carbon adsorbing acidic gases and causes the gas to pass through its inside so as to remove smelling ingredients through adsorption, arranged in this order along with the exhaust gas duct 20. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は排ガス処理装置に関し、特に合成樹脂製品を燃焼する燃焼室から排出された排ガスを乾式で処理する排ガス処理装置に関するものである。   The present invention relates to an exhaust gas treatment device, and more particularly to an exhaust gas treatment device that treats exhaust gas discharged from a combustion chamber that burns a synthetic resin product in a dry manner.

従来から、都市ごみ焼却炉等からの焼却排ガス中に含まれるダイオキシン等の有害物質を除去処理する排ガス処理装置として、(1)排ガスに活性炭を混入した消石灰を吹き込んで、活性炭にダイオキシン等を吸着させた後、バグフィルタにて集塵除去するようにしたもの、(2)バグフィルタにて集塵した後、活性炭充填塔に通してダイオキシン等を吸着除去するようにしたもの、(3)バグフィルタにて集塵した後、脱硫触媒充填塔に通して脱硫触媒にてダイオキシン等を酸化分解させるようにしたもの、(4)排ガス中に消石灰とゼオライトまたはゼオライトを主成分とする混合物よりなる吸着剤を吹き込んだ後、バグフィルタにて集塵し、その後脱硝触媒充填塔に通して窒素酸化物を脱硝反応にて無害化するようにしたものが知られている(例えば、特許文献1参照。)。   Conventionally, as an exhaust gas treatment device that removes harmful substances such as dioxins contained in incineration exhaust gas from municipal waste incinerators, etc. (1) Injecting slaked lime mixed with activated carbon into the exhaust gas and adsorbing dioxin etc. on the activated carbon (2) Dust collected by bag filter, (2) Dust collected by bag filter, passed through activated charcoal packed tower to remove dioxin, etc., (3) Bug Dust collected by a filter and then passed through a desulfurization catalyst packed tower to oxidatively decompose dioxin and the like with the desulfurization catalyst. After blowing the agent, dust is collected with a bag filter, and then passed through a denitration catalyst packed tower to make nitrogen oxides harmless by denitration reaction. Are (e.g., see Patent Document 1.).

また、廃棄物処理炉からの排ガスを160〜170℃に冷却した後、バグフィルタ装置にて集塵し、その後排ガス洗浄装置で窒素酸化物等の有害成分を除去するようにした排ガス処理装置などに適用されるバグフィルタ装置として、腐蝕性ガスが結露することがないように、かつ排ガス中にダイオキシン除去のために活性炭等の発火性助剤が混入されている場合でも発火することがないように、ホッパー部を局部的に高温の部分を生じさせることなく加熱する加熱手段を設けたものも知られている(例えば、特許文献2参照。)。
特開平10−249160号公報 特開2001−347120号公報
Further, after exhaust gas from the waste treatment furnace is cooled to 160 to 170 ° C., dust is collected by a bag filter device, and then harmful components such as nitrogen oxides are removed by an exhaust gas cleaning device, etc. As a bag filter device applied to, so that corrosive gas does not condense, and even if ignitable auxiliary agents such as activated carbon are mixed in the exhaust gas to remove dioxin, it does not ignite In addition, there is also known one provided with heating means for heating the hopper without locally generating a high-temperature part (see, for example, Patent Document 2).
Japanese Patent Laid-Open No. 10-249160 JP 2001-347120 A

ところで、PPやABS樹脂などから成る合成樹脂製品を普通に焼却した場合には、特に排ガス中にダイオキシンが含まれ易いことと多くの臭い成分が含まれるために嫌な臭いがすることが重要な問題となる。そこで、ダイオキシンの発生量を抑制するため低温で焼却処理することが考えられるが、その場合でも上記特許文献1に開示されたような構成の排ガス処理装置によって排ガスの処理を行っても、ダイオキシンやダストの排出量を規定値以下にしかつ硫黄酸化物や塩化水素などの各種臭い成分についても確実に規定値以下にすることは困難であるという問題がある。   By the way, when a synthetic resin product made of PP, ABS resin or the like is normally incinerated, it is particularly important that the exhaust gas easily contains dioxin and has a bad smell because many odorous components are included. It becomes a problem. Therefore, in order to suppress the generation amount of dioxin, it is conceivable to incinerate at a low temperature. Even in that case, even if the exhaust gas treatment apparatus having the configuration as disclosed in Patent Document 1 is used, the dioxin or There is a problem that it is difficult to reduce the amount of dust emission to a specified value or less and to reliably reduce the odor components such as sulfur oxide and hydrogen chloride to a specified value or less.

なお、排ガス中の臭い成分を確実に除去する手段として、湿式スクラバーを用いることは従来から知られているが、湿式の場合は大量の排水処理が必要となるため、環境上もコスト的にも好ましくないという問題がある。   As a means for reliably removing odorous components in exhaust gas, it has been conventionally known to use a wet scrubber, but in the case of a wet type, a large amount of wastewater treatment is required. There is a problem that it is not preferable.

本発明は、上記従来の問題点に鑑み、合成樹脂製品の燃焼排ガス中に含まれるダイオキシンや臭い成分を乾式処理によって確実に除去することができる排ガス処理を実現することを課題とする。   In view of the above-described conventional problems, an object of the present invention is to realize an exhaust gas treatment capable of reliably removing dioxins and odor components contained in a combustion exhaust gas of a synthetic resin product by a dry treatment.

本発明の排ガス処理装置は、上記課題を解決するため、合成樹脂製品を燃焼する燃焼室から排出された200℃以下の排ガスの処理装置であって、排ガスの排出通路に沿って、排ガス中に活性炭と消石灰の混合粉末を噴霧供給する処理粉末供給部と、排ガス中の粉末を除去するバグフィルタ装置と、内部に排ガスを通して臭い成分を吸着除去する活性炭吸着部とをこの順に配設したものである。   In order to solve the above problems, an exhaust gas treatment apparatus of the present invention is a treatment apparatus for exhaust gas of 200 ° C. or less discharged from a combustion chamber that burns a synthetic resin product, and is disposed in exhaust gas along an exhaust gas discharge passage. A treatment powder supply unit that sprays and supplies mixed powder of activated carbon and slaked lime, a bag filter device that removes powder in exhaust gas, and an activated carbon adsorption unit that adsorbs and removes odorous components through exhaust gas inside are arranged in this order. is there.

この構成によると、排ガス中に噴霧供給した活性炭粉末によってダイオキシンが吸着されるとともに排ガス中の酸性ガスも消石灰粉末と反応して中和され、これらの混合粉末をダストとともにバグフィルタ装置にて除去することでダイオキシンや酸性ガスを排ガスから除去でき、さらに排ガスを活性炭吸着部に通すことにより排ガス中に残った臭い成分を確実に吸着除去することができ、したがって排水処理の必要な湿式スクラバーを用いることなく、ダイオキシンやダストの排出量を規定値以下にしかつ硫黄酸化物や塩化水素などの各種臭い成分についても確実に規定値以下にすることができる。   According to this configuration, the activated carbon powder sprayed into the exhaust gas adsorbs dioxin and the acid gas in the exhaust gas reacts with the slaked lime powder to be neutralized, and these mixed powders are removed together with dust with a bag filter device. Dioxin and acid gas can be removed from the exhaust gas, and the odorous components remaining in the exhaust gas can be reliably adsorbed and removed by passing the exhaust gas through the activated carbon adsorption part, so use a wet scrubber that requires wastewater treatment. In addition, the emission amount of dioxin and dust can be reduced below the specified value, and various odor components such as sulfur oxide and hydrogen chloride can be reliably reduced below the specified value.

また、処理粉末供給部の直後の排出通路にラインミキサーを配設すると、排ガスの全体と処理粉末を均等にかつ何回も接触させることができ、排ガス中のダイオキシンの吸着及び酸性ガスの中和を確実に行うことができる。   In addition, if a line mixer is installed in the discharge passage immediately after the treated powder supply unit, the entire exhaust gas can be brought into contact with the treated powder evenly and repeatedly, so that adsorption of dioxins in the exhaust gas and neutralization of acid gas are possible. Can be performed reliably.

また、活性炭吸着部が、前段に中性用活性炭層を、後段に酸性用活性炭層を配設して成ると、前段で排ガス中に残った微細粉塵などの微粒子を吸着した後、後段で臭い成分である酸性微粒子を吸着除去することができる。   In addition, when the activated carbon adsorbing part is configured with a neutral activated carbon layer in the former stage and an acidic activated carbon layer in the latter stage, after adsorbing fine particles such as fine dust remaining in the exhaust gas in the former stage, it smells in the latter stage. It is possible to adsorb and remove acidic fine particles as a component.

また、バグフィルタ装置と活性炭吸着部との間に排ガスを冷却する熱交換器を配設すると、排ガス温度を、例えば40℃程度まで冷却することができ、活性炭吸着部における吸着作用を効率的に行うことができるとともに排ガスの排出温度を低温して白煙化を防止することができる。   Further, if a heat exchanger for cooling the exhaust gas is disposed between the bag filter device and the activated carbon adsorption unit, the exhaust gas temperature can be cooled to, for example, about 40 ° C., and the adsorption action in the activated carbon adsorption unit can be efficiently performed. It can be performed and the exhaust gas discharge temperature can be lowered to prevent white smoke.

また、活性炭吸着部の出口に臭気センサを配設し、活性炭吸着部から排出された排ガスを、臭気センサの検出結果に応じて外部への排出と処理粉末供給部の入口への還流の何れかに切り換える流路切換装置を配設すると、外部に排出する排ガスを確実に臭いのないものにすることができる。   Also, an odor sensor is provided at the outlet of the activated carbon adsorption unit, and the exhaust gas discharged from the activated carbon adsorption unit is either discharged outside or returned to the inlet of the treated powder supply unit according to the detection result of the odor sensor. When the flow path switching device for switching to is provided, the exhaust gas discharged to the outside can be surely free from odor.

本発明の排ガス処理装置によれば、合成樹脂製品を低温で燃焼した排ガスを、排水処理の必要のない乾式処理によって、ダストやダイオキシンの排出量を規定値以下にしかつ各種臭い成分についても確実に規定値以下にして排出することができる。   According to the exhaust gas treatment apparatus of the present invention, exhaust gas produced by burning a synthetic resin product at a low temperature is subjected to dry treatment that does not require wastewater treatment, and the amount of dust and dioxin emission is reduced to a specified value or less, and various odor components are also reliably obtained. It can be discharged below the specified value.

以下、本発明の排ガス処理装置を、事務機器用の合成樹脂製品の燃焼実験装置に適用した一実施形態について、図1〜図4を参照して説明する。   Hereinafter, an embodiment in which the exhaust gas treatment apparatus of the present invention is applied to a synthetic resin product combustion experiment apparatus for office equipment will be described with reference to FIGS.

図1及び図3と図4において、1は事務機器用の合成樹脂製品から成る燃焼対象物2を燃焼する燃焼室で、燃焼対象物2を載置して燃焼させる燃焼台3が下部の中央に設置されている。燃焼室1の側壁には、図3に示すように、燃焼状態を視認するため、耐熱ガラス製の観測窓4が配設されている。また、天井部の中央に排気口5が設けられ、側壁の下端部に燃焼用空気を導入するグリル開口6が設けられている。排気口5には、外部に排出する排ガス温度を外気の導入によって調整するために、外気導入調整弁7を介して外気導入口8が接続されている。   1, 3, and 4, 1 is a combustion chamber for burning a combustion object 2 made of a synthetic resin product for office equipment, and a combustion table 3 on which the combustion object 2 is placed and combusted is located at the center in the lower part. Is installed. As shown in FIG. 3, an observation window 4 made of heat-resistant glass is disposed on the side wall of the combustion chamber 1 in order to visually check the combustion state. An exhaust port 5 is provided at the center of the ceiling, and a grill opening 6 for introducing combustion air is provided at the lower end of the side wall. An outside air introduction port 8 is connected to the exhaust port 5 via an outside air introduction adjustment valve 7 in order to adjust the temperature of exhaust gas discharged outside by introduction of outside air.

燃焼室1の一側壁の上部と下部にガス循環用の流出口9と流入口10が設けられ、流出口9から燃焼室1内の雰囲気を引き出してバグフィルタ装置11に通し、雰囲気中の煤を除去した後循環ファン12にて流入口10から燃焼室1内に押し込み、燃焼室1内の雰囲気を煤を除去して循環させることで、燃焼室1内が低酸素濃度状態となるようにしている。これにより、燃焼対象物2の燃焼を抑制し、燃焼室1内が高温にならないようにしている。具体的には、燃焼室1の上部の排気口5近傍の雰囲気温度を200℃以下に制御するように構成されている。   An outlet 9 and an inlet 10 for gas circulation are provided at an upper part and a lower part of one side wall of the combustion chamber 1, and the atmosphere in the combustion chamber 1 is drawn from the outlet 9 and passed through the bag filter device 11. Is removed, and the circulation fan 12 is pushed into the combustion chamber 1 from the inlet 10 to circulate the atmosphere in the combustion chamber 1 by removing soot so that the combustion chamber 1 is in a low oxygen concentration state. ing. Thereby, combustion of the combustion target object 2 is suppressed and the inside of the combustion chamber 1 is made not to become high temperature. Specifically, the ambient temperature in the vicinity of the exhaust port 5 at the top of the combustion chamber 1 is controlled to 200 ° C. or lower.

燃焼室1の上部には、燃焼室1内の雰囲気温度が異常に上昇した時に水消火するように、スプリンクラー13が配設され、開閉制御弁14を介して消火設備15に接続されている。開閉制御弁14は、排気口5の近傍に配置した温度検知器16及び流出口9とバグフィルタ装置11の間に配置した温度検知器17の検知温度がそれぞれ所定温度以上になると開弁するように構成されている。   A sprinkler 13 is disposed above the combustion chamber 1 so as to extinguish water when the atmospheric temperature in the combustion chamber 1 rises abnormally, and is connected to a fire extinguishing facility 15 via an open / close control valve 14. The opening / closing control valve 14 opens when the temperature detector 16 disposed in the vicinity of the exhaust port 5 and the temperature detected by the temperature detector 17 disposed between the outlet 9 and the bag filter device 11 are each equal to or higher than a predetermined temperature. It is configured.

燃焼室1には、内部雰囲気のHCl濃度と、CO濃度とO2 濃度の比をモニタリングするため、HCl計18と、CO/O2 計19が設置されている。 The combustion chamber 1 is provided with an HCl meter 18 and a CO / O 2 meter 19 for monitoring the HCl concentration of the internal atmosphere and the ratio of the CO concentration and the O 2 concentration.

排気口5には排ガス管路20が接続され、この排ガス管路20には、図2及び図3と図4に示すように、排ガスの温度を検知する温度検知器21と、排ガス中に活性炭と消石灰の混合粉末を噴霧供給する処理粉末供給部22と、排ガスの流量調整弁23と、排ガス中の粉末を除去するバグフィルタ装置24と、排ガスを外気と熱交換させて冷却する熱交換器25と、排気ファン26と、内部に排ガスを通して臭い成分を吸着除去する活性炭吸着部27とがこの順に配設されている。   An exhaust gas pipe 20 is connected to the exhaust port 5. As shown in FIGS. 2, 3, and 4, the exhaust gas pipe 20 includes a temperature detector 21 that detects the temperature of the exhaust gas, and activated carbon in the exhaust gas. Powder processing unit 22 for spraying mixed powder of slaked lime and slaked lime, a flow rate adjusting valve 23 for exhaust gas, a bag filter device 24 for removing powder in the exhaust gas, and a heat exchanger for cooling the exhaust gas by heat exchange with the outside air 25, an exhaust fan 26, and an activated carbon adsorbing portion 27 for adsorbing and removing odorous components through exhaust gas inside are arranged in this order.

温度検知器21にて検出された排ガス管路20を通る排ガスの温度に応じて、外気導入調整弁7と、流量調整弁23と、後述の熱交換器25の送風ファン25bを制御するように構成されている。   According to the temperature of the exhaust gas passing through the exhaust gas pipe line 20 detected by the temperature detector 21, the outside air introduction adjustment valve 7, the flow rate adjustment valve 23, and the blower fan 25b of the heat exchanger 25 described later are controlled. It is configured.

処理粉末供給部22は、活性炭と消石灰の粉末を50:50で混合した混合粉末を収容した収容タンク22aと、圧送ファン22bと、排ガス管路20に設けた処理粉末供給口と圧送ファン22bとを接続するとともに、中間に収容タンク22aの排出口が接続された搬送管22cにて構成され、圧送ファン22bから搬送管22cを通して排ガス管路20内に向けて圧送する空気流に乗せて混合粉末を空気搬送し、排ガス管路20内に噴霧供給するように構成されている。   The treatment powder supply unit 22 includes a storage tank 22a containing a mixed powder obtained by mixing activated carbon and slaked lime powder at 50:50, a pressure feed fan 22b, a treatment powder supply port provided in the exhaust gas pipeline 20, and a pressure feed fan 22b. In addition, the mixed powder is formed by a transport pipe 22c connected to the discharge port of the storage tank 22a in the middle, and is put on an air flow that is pumped from the pressure feed fan 22b through the transport pipe 22c into the exhaust gas pipe 20. Are pneumatically conveyed and sprayed into the exhaust gas pipe 20.

バグフィルタ装置24は、ホッパー部24a内に収容配置したバグフィルタ24bにて排ガス中の煤や噴霧供給された粉末を分離回収するように構成され、かつコンプレッサ28から供給される圧縮空気をバグフィルタ24bに排ガス流通方向とは逆方向にパルス状に噴出させてバグフィルタ24bを逆洗してホッパー部24a内に落下回収する逆洗機構24cを備えている。なお、バグフィルタ装置11も同様にホッパー部11aとバグフィルタ11bと逆洗機構11cを備えている。   The bag filter device 24 is configured to separate and recover the soot in the exhaust gas and the powder supplied by spraying with the bag filter 24b accommodated in the hopper portion 24a, and the compressed air supplied from the compressor 28 to the bag filter. 24b is provided with a backwashing mechanism 24c that jets in a pulse shape in the direction opposite to the exhaust gas flow direction, backwashes the bag filter 24b, and drops and recovers the bag filter 24b into the hopper 24a. The bag filter device 11 similarly includes a hopper portion 11a, a bag filter 11b, and a backwash mechanism 11c.

熱交換器25は、熱交換部25aと、熱交換部25aに熱交換用外気を送風する送風ファン25bと、外気中の塵を除塵して送風ファン25bに送給するフィルタ25cと、送風ファン25bのインバータ制御部25dを備えており、インバータ制御部25dに温度検知器21の検出信号が入力されている。   The heat exchanger 25 includes a heat exchange unit 25a, a blower fan 25b that blows outside air for heat exchange to the heat exchange unit 25a, a filter 25c that removes dust in the outside air and supplies the dust to the blower fan 25b, and a blower fan An inverter control unit 25d of 25b is provided, and a detection signal of the temperature detector 21 is input to the inverter control unit 25d.

活性炭吸着部27は、粉末状、破砕炭状、粒状(ペレット状)等の活性炭を充填した固定床式で、前段の普通炭から成る中性用活性炭層27aと後段の酸性ガス吸着炭からなる酸性用活性炭層27bとを備え、排ガス中に残った臭い成分である酸性微粒子を吸着除去するように構成されている。そして、この活性炭吸着部27を通過した排ガスは、大気中に放出される。   The activated carbon adsorbing unit 27 is a fixed bed type filled with activated carbon such as powder, crushed charcoal, granular (pellet), etc., and is composed of a neutral activated carbon layer 27a made of preceding ordinary charcoal and a subsequent acidic gas adsorbing charcoal. An acidic activated carbon layer 27b, and configured to adsorb and remove acidic fine particles, which are odorous components remaining in the exhaust gas. And the exhaust gas which passed this activated carbon adsorption part 27 is discharge | released in air | atmosphere.

なお、図2に仮想線で示すように、活性炭吸着部27の出口に臭気センサ29を配設するとともに、排ガス放出口の手前に流路切換装置30を設け、臭気センサ29にて排ガス中に所定以上の臭い成分が残っていた場合に、流路切換装置30を作動させて、還流管路31を通して排ガスを処理粉末供給部22の手前位置に還流させ、再度処理を繰り返すように構成しても良い。   2, an odor sensor 29 is provided at the outlet of the activated carbon adsorption unit 27, and a flow path switching device 30 is provided in front of the exhaust gas discharge port. When the odor component more than a predetermined amount remains, the flow path switching device 30 is operated, the exhaust gas is recirculated to the position before the processing powder supply unit 22 through the reflux line 31, and the process is repeated again. Also good.

また、処理粉末供給部22の出口近傍にラインミキサー32を配設することで、排ガス中に活性炭と消石灰を均等に分散させ、排ガスの全体に対して活性炭と消石灰を効果的に接触させ、排ガス中のダイオキシンの吸着や酸性ガスの中和反応が確実に行われるようにするのが好ましい。   Further, by disposing the line mixer 32 in the vicinity of the outlet of the treated powder supply unit 22, the activated carbon and the slaked lime are evenly dispersed in the exhaust gas, and the activated carbon and the slaked lime are effectively brought into contact with the entire exhaust gas. It is preferable to ensure that the adsorption of dioxin and the neutralization reaction of the acid gas are performed.

次に、動作について説明する。燃焼台3上に合成樹脂製品から成る燃焼対象物2を載置して着火し、燃焼を開始する。その際、燃焼初期には排気ファン26は作動せず、排気口5から排気することなく、循環ファン12だけを作動させ、燃焼室1内の雰囲気を循環させることで、比較的低温で自然燃焼させる。その結果、煤を多量に発生するが、発生した煤は排ガスが循環される間にバグフィルタ装置11で除去される。また、循環される排ガスの温度を温度検知器17にて検出し、温度に応じて循環ファン12を作動制御することで、比較的低温での自然燃焼を維持している。   Next, the operation will be described. A combustion object 2 made of a synthetic resin product is placed on the combustion table 3 and ignited to start combustion. At that time, the exhaust fan 26 does not operate at the initial stage of combustion, and only the circulation fan 12 is operated without exhausting from the exhaust port 5 and the atmosphere in the combustion chamber 1 is circulated. Let As a result, a large amount of soot is generated, but the generated soot is removed by the bag filter device 11 while the exhaust gas is circulated. Further, the temperature of the circulated exhaust gas is detected by the temperature detector 17, and the operation of the circulation fan 12 is controlled according to the temperature, thereby maintaining natural combustion at a relatively low temperature.

また、燃焼室1内で過大な燃焼状態となって雰囲気温度が異常に高くなり、排気口5の近傍の温度検知器16による検出温度が200℃を超えると、開閉制御弁14が開弁されて消火設備15からスプリンクラー13に消火水が供給され、水が噴霧されて消火される。これにより、ガラス窓から成る観測窓4を有する燃焼室1においても、安全に燃焼実験を行うことができる。また、燃焼室1内の雰囲気をHCl計18及びCO/O2 計19にてモニタリングしているので、この燃焼室1内に作業者が入室する場合の安全も確保されている。 Further, when the combustion chamber 1 is in an excessive combustion state and the ambient temperature becomes abnormally high, and the temperature detected by the temperature detector 16 near the exhaust port 5 exceeds 200 ° C., the opening / closing control valve 14 is opened. Then, fire extinguishing water is supplied from the fire extinguishing equipment 15 to the sprinkler 13, and water is sprayed to extinguish the fire. Thereby, also in the combustion chamber 1 which has the observation window 4 which consists of glass windows, a combustion experiment can be performed safely. Further, since the atmosphere in the combustion chamber 1 is monitored by the HCl meter 18 and the CO / O 2 meter 19, safety is ensured when an operator enters the combustion chamber 1.

燃焼室1での低温燃焼状態が安定すると、上記循環ファン12による排ガスの循環によるその燃焼状態を維持しつつ、排気ファン26を作動させ、排気口5から排ガスを吸引して排ガス管路20に排出する。循環させる排ガス流量と排気口5から排出する排ガス流量の比は、循環7:排出3程度である。この排気口5から排出される排ガスは、例えば最大40m3 N/min程度で、その組成にはSO2 を60ppm、HClを1053ppm、ダイオキシンを10ng−TEQ/m3 N、ダストを240mg/m3 N程度含有している。また、ガス温度が40〜200℃となるように、温度検知器21の検知温度に応じて外気導入調整弁7の開度を調整し、また流量調整弁23の開度調整にてバグフィルタ装置24の過熱防止を図っている。 When the low-temperature combustion state in the combustion chamber 1 is stabilized, the exhaust fan 26 is operated while maintaining the combustion state due to the circulation of the exhaust gas by the circulation fan 12, and the exhaust gas is sucked from the exhaust port 5 to the exhaust gas pipe 20. Discharge. The ratio of the exhaust gas flow rate to be circulated and the exhaust gas flow rate discharged from the exhaust port 5 is about circulation 7: discharge 3. The exhaust gas discharged from the exhaust port 5 has, for example, a maximum of about 40 m 3 N / min, and has a composition of SO 2 of 60 ppm, HCl of 1053 ppm, dioxin of 10 ng-TEQ / m 3 N, and dust of 240 mg / m 3. About N is contained. Further, the opening degree of the outside air introduction adjustment valve 7 is adjusted according to the temperature detected by the temperature detector 21 so that the gas temperature becomes 40 to 200 ° C., and the bag filter device is adjusted by adjusting the opening degree of the flow rate adjustment valve 23. 24 is prevented from overheating.

排ガス管路20に排出された排ガスに対して、最初に処理粉末供給部22にて活性炭と消石灰の混合粉末が噴霧供給される。これら活性炭と消石灰が排ガスと接触し、ダイオキシンが活性炭粉末に吸着除去されるとともに酸性ガスが消石灰と反応して中和吸収される。この混合粉末の供給量は、例えば100〜300mg/m3 程度で充分な効果を発揮する。また、混合粉末の供給直後に、ラインミキサー32にて排ガスと混合粉末の攪拌混合行うと、排ガスの全体とこれらの粉末の接触機会が増加し、これらの作用が促進され、より効果的に吸着・中和が行われる。 First, a mixed powder of activated carbon and slaked lime is sprayed and supplied to the exhaust gas discharged to the exhaust gas pipe 20 by the processing powder supply unit 22. The activated carbon and slaked lime come into contact with the exhaust gas, and dioxins are adsorbed and removed by the activated carbon powder, and the acidic gas reacts with the slaked lime to be neutralized and absorbed. The supply amount of the mixed powder exhibits a sufficient effect, for example, at about 100 to 300 mg / m 3 . Further, when the exhaust gas and the mixed powder are stirred and mixed immediately after the supply of the mixed powder, the opportunity of contact between the exhaust gas and these powders increases, and these actions are promoted and more effectively adsorbed. -Neutralization is performed.

ダイオキシンを吸着した活性炭粉末及び酸性ガスと中和反応した消石灰粉末は、次のバグフィルタ装置24にて排ガスから除去される。次いで、排ガスは熱交換器25にて外気と熱交換されて80℃程度から40℃程度まで冷却される。このように排ガス温度が40℃以下に冷却されることで、次の活性炭吸着部27での吸着が効果的に行われる。   The activated carbon powder that has adsorbed dioxin and the slaked lime powder that has been neutralized with the acid gas are removed from the exhaust gas by the next bag filter device 24. Next, the exhaust gas is heat-exchanged with the outside air in the heat exchanger 25 and cooled from about 80 ° C. to about 40 ° C. Thus, by the exhaust gas temperature being cooled to 40 ° C. or less, the next adsorption at the activated carbon adsorption unit 27 is effectively performed.

次いで、排ガスは活性炭吸着部27の前段の中性用活性炭層27aにて排ガス中に残った微細粉塵などの微粒子が吸着され、さらに後段の酸性用活性炭層27bにて臭い成分であるSO2 やHClなどの酸性微粒子が確実に吸着除去される。このように清浄化され、臭い成分を除去された排ガスが大気中に放出される。 Next, the exhaust gas is adsorbed with fine particles such as fine dust remaining in the exhaust gas in the neutral activated carbon layer 27a in the previous stage of the activated carbon adsorption unit 27, and further in the subsequent acidic activated carbon layer 27b, the odor component SO 2 or Acidic fine particles such as HCl are reliably removed by adsorption. The exhaust gas thus purified and from which odorous components are removed is released into the atmosphere.

以上の処理により、例えば上記排気口5での排ガス組成に比較して、SO2 を60ppmから40ppm以下に、HClを1053ppmから430ppm以下に、ダイオキシンを10ng−TEQ/m3 Nから5ng−TEQ/m3 N以下に、ダストを240mg/m3 Nから10mg/m3 N以下に低減することができる。かくして、排水処理の必要な湿式スクラバーを用いることなく、環境基準を満たした状態で大気中に放出することができる。 By the above treatment, for example, compared to the exhaust gas composition at the exhaust port 5, SO 2 is reduced from 60 ppm to 40 ppm, HCl is reduced from 1053 ppm to 430 ppm, dioxin is changed from 10 ng-TEQ / m 3 N to 5 ng-TEQ / m to 3 N or less, it is possible to reduce the dust from 240 mg / m 3 N below 10 mg / m 3 N. Thus, without using a wet scrubber that requires wastewater treatment, it can be released into the atmosphere in a state that satisfies environmental standards.

上記実施形態の説明では、処理粉末供給部22から供給する混合粉末の活性炭と消石灰の比率が50:50の例を示したが、燃焼室1の排気口5から排出される排ガスの性質に応じて適宜設定すれば良く、例えば酸性ガスの濃度が高い場合には消石灰の組成を高くすれば良いことは言うまでもない。また、活性炭吸着部27に、中性用活性炭層27aと酸性用活性炭層27bを設けた例を示したが、さらなアルカリ用活性炭層などを設けて良いことも言うまでもない。   In the description of the above embodiment, an example in which the ratio of the activated carbon and slaked lime of the mixed powder supplied from the processing powder supply unit 22 is 50:50 is shown, but depending on the nature of the exhaust gas discharged from the exhaust port 5 of the combustion chamber 1 Needless to say, the composition of slaked lime may be increased when the concentration of acid gas is high, for example. Moreover, although the example which provided the activated carbon layer 27a for neutrality and the activated carbon layer 27b for acid in the activated carbon adsorption part 27 was shown, it cannot be overemphasized that the activated carbon layer for alkalis etc. may be provided.

また、上記実施形態は、本発明の排ガス処理装置を事務機器用の合成樹脂製品から成る燃焼対象物2の燃焼実験装置における燃焼室1から排出される排ガスの処理に適用した例を示したが、本発明の排ガス処理装置は各種合成樹脂製品の燃焼処理装置の排ガス処理にも当然適用できるとともに、その効果を発揮できることは改めて説明するまでもなく明らかである。   Moreover, although the said embodiment showed the example which applied the waste gas processing apparatus of this invention to the process of the waste gas discharged | emitted from the combustion chamber 1 in the combustion experiment apparatus of the combustion target object 2 which consists of synthetic resin products for office equipments, Of course, the exhaust gas treatment apparatus of the present invention can be applied to the exhaust gas treatment of a combustion treatment apparatus for various synthetic resin products, and the effect can be demonstrated without needing to be described again.

本発明にかかる排ガス処理装置は、合成樹脂製品を低温で焼却処理した場合の排ガスを、乾式処理にてダイオキシンやダストの排出量を規定値以下にしかつ各種臭い成分についても確実に規定値以下に処理すことができ、合成樹脂製品の燃焼処理装置における排ガス処理に有用である。   The exhaust gas treatment apparatus according to the present invention makes it possible to reduce the emission of dioxin and dust to a specified value or less by dry processing, and to ensure that the various odorous components are also to a specified value or less. It can be treated and is useful for exhaust gas treatment in a combustion treatment apparatus for synthetic resin products.

本発明の排ガス処理装置の一実施形態を適用した燃焼実験装置の燃焼室回りの概略構成図である。1 is a schematic configuration diagram around a combustion chamber of a combustion experimental apparatus to which an embodiment of an exhaust gas treatment apparatus of the present invention is applied. 同実施形態の排ガス処理部の概略構成図である。It is a schematic block diagram of the waste gas processing part of the embodiment. 同実施形態の燃焼実験装置の平面配置図である。FIG. 3 is a plan layout view of the combustion experiment apparatus of the same embodiment. 図3のA−A矢視立面図である。It is an AA arrow elevational view of FIG.

符号の説明Explanation of symbols

1 燃焼室
20 排ガス管路
22 処理粉末供給部
24 バグフィルタ装置
25 熱交換器
27 活性炭吸着部
27a 中性用活性炭層
27b 酸性用活性炭層
29 臭気センサ
30 流路切換装置
32 ラインミキサー
DESCRIPTION OF SYMBOLS 1 Combustion chamber 20 Exhaust gas pipe 22 Process powder supply part 24 Bag filter apparatus 25 Heat exchanger 27 Activated carbon adsorption part 27a Activated carbon layer for neutral 27b Activated carbon layer for acid 29 Odor sensor 30 Flow path switching device 32 Line mixer

Claims (5)

合成樹脂製品を燃焼する燃焼室から排出された200℃以下の排ガスの処理装置であって、排ガスの排出通路に沿って、排ガス中に活性炭と消石灰の混合粉末を噴霧供給する処理粉末供給部と、排ガス中の粉末を除去するバグフィルタ装置と、内部に排ガスを通して臭い成分を吸着除去する活性炭吸着部とをこの順に配設したことを特徴とする排ガス処理装置。 An apparatus for treating exhaust gas of 200 ° C. or less exhausted from a combustion chamber that burns a synthetic resin product, wherein a treatment powder supply unit that sprays a mixed powder of activated carbon and slaked lime into the exhaust gas along an exhaust gas exhaust passage; An exhaust gas treatment apparatus comprising: a bag filter device that removes powder in exhaust gas; and an activated carbon adsorbing portion that adsorbs and removes odorous components through the exhaust gas in this order. 処理粉末供給部の直後の排出通路にラインミキサーを配設したことを特徴とする請求項1記載の排ガス処理装置。 The exhaust gas treatment apparatus according to claim 1, wherein a line mixer is disposed in the discharge passage immediately after the treated powder supply unit. 活性炭吸着部は、前段に中性用活性炭層を、後段に酸性用活性炭層を配設して成ることを特徴とする請求項1又は2記載の排ガス処理装置。 3. The exhaust gas treatment apparatus according to claim 1, wherein the activated carbon adsorbing portion is configured such that a neutral activated carbon layer is disposed in a preceding stage and an acidic activated carbon layer is disposed in a subsequent stage. バグフィルタ装置と活性炭吸着部との間に排ガスを冷却する熱交換器を配設したことを特徴とする請求項1記載の排ガス処理装置。 The exhaust gas treatment apparatus according to claim 1, wherein a heat exchanger for cooling the exhaust gas is disposed between the bag filter device and the activated carbon adsorption part. 活性炭吸着部の出口に臭気センサを配設し、活性炭吸着部から排出された排ガスを、臭気センサの検出結果に応じて外部への排出と処理粉末供給部の入口への還流の何れかに切り換える流路切換装置を配設したことを特徴とする請求項1記載の排ガス処理装置。
An odor sensor is provided at the outlet of the activated carbon adsorption unit, and the exhaust gas discharged from the activated carbon adsorption unit is switched to either external discharge or reflux to the inlet of the treated powder supply unit according to the detection result of the odor sensor. The exhaust gas treatment apparatus according to claim 1, further comprising a flow path switching device.
JP2003309014A 2003-09-01 2003-09-01 Exhaust gas treatment apparatus Pending JP2005074333A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007061719A (en) * 2005-08-30 2007-03-15 Sumitomo Heavy Ind Ltd Deodorization apparatus
RU2466930C2 (en) * 2007-01-12 2012-11-20 Акцо Нобель Н.В. Method of chlorine dioxide obtaining
CN113521943A (en) * 2021-06-29 2021-10-22 宁波明讯实业有限公司 Small-air-volume automobile spray paint and automobile plastic modified waste gas treatment process
JP7496462B1 (en) 2023-08-10 2024-06-06 三菱重工環境・化学エンジニアリング株式会社 Fly ash circulation device

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007061719A (en) * 2005-08-30 2007-03-15 Sumitomo Heavy Ind Ltd Deodorization apparatus
RU2466930C2 (en) * 2007-01-12 2012-11-20 Акцо Нобель Н.В. Method of chlorine dioxide obtaining
CN113521943A (en) * 2021-06-29 2021-10-22 宁波明讯实业有限公司 Small-air-volume automobile spray paint and automobile plastic modified waste gas treatment process
JP7496462B1 (en) 2023-08-10 2024-06-06 三菱重工環境・化学エンジニアリング株式会社 Fly ash circulation device

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