JP2006043498A - Washing/adsorption type deodorizer - Google Patents

Washing/adsorption type deodorizer Download PDF

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JP2006043498A
JP2006043498A JP2004224048A JP2004224048A JP2006043498A JP 2006043498 A JP2006043498 A JP 2006043498A JP 2004224048 A JP2004224048 A JP 2004224048A JP 2004224048 A JP2004224048 A JP 2004224048A JP 2006043498 A JP2006043498 A JP 2006043498A
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adsorption
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odor
reaction tower
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Masakazu Nakamura
正和 中村
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ECO UP KK
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a washing/adsorption type deodorizer capable of preventing corrosion of and damage to a blower due to humidity and dust and enhancing the efficiency of deodorization in a cleaning tower and an adsorption/reaction tower. <P>SOLUTION: A temperature sensor 8 and a cooler 9 are disposed in an air bubble tank 3 communicating with a garbage disposer 1 so as to control the temperature of washing water 4 to <40°C with a control panel 10 based on a sensor signal. A pipe 6 is connected to a gas filling part 5 of an air bubble tank 3, the top end side of the pipe is connected to the bottom surface of the adsorption/reaction tower 7, and a suction fan 11 which sucks a filling gas and force-feeds the gas to the adsorption/reaction tower 7 is disposed in the middle between the air bubble tank 3 and the adsorption/reaction tower 7 in the pipe 6. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、臭気ガスを洗浄した後、臭気を吸着除去する洗浄吸着式脱臭装置に関するものである。   The present invention relates to a cleaning adsorption deodorizing apparatus that adsorbs and removes odor after cleaning odor gas.

従来、生ゴミ処理などで生じるガス中の臭気を消去する装置としては、活性炭吸着式、曝気洗浄式、送風循環式、触媒燃焼方式、生物脱方式などがある(例えば、特許文献1〜特許文献3参照)。しかし、活性炭吸着方式では、臭気ガスの温度や湿度が高いほど吸着量が低下し、活性炭表面に粉塵が付着すると吸着能力が十分に発揮されなくなる。また、曝気洗浄方式では、洗浄水が滞留した状態の水槽で高温ガス(40〜70℃)を連続処理した場合、水温が上昇して一旦溶出した臭気が再び揮発するため、脱臭能力が低下する。さらに、送風循環方式では、特に腐食性(酸塩基性)湿度ガス又は高粉塵ガスを処理する場合、送風機の中に水滴が溜まって腐食したり、あるいは高負荷及び漏電を誘発させるおそれがあり、また、送風機の羽根部分にも粉塵が付着して能力低下や故障の原因になる。   Conventionally, there are activated carbon adsorption type, aeration cleaning type, blower circulation type, catalytic combustion type, biological desorption type, etc. as an apparatus for eliminating odor in gas generated by garbage disposal etc. (for example, Patent Document 1 to Patent Document) 3). However, in the activated carbon adsorption system, the adsorption amount decreases as the temperature or humidity of the odor gas increases, and if the dust adheres to the activated carbon surface, the adsorption ability is not fully exhibited. Further, in the aeration cleaning method, when high temperature gas (40 to 70 ° C.) is continuously processed in a water tank in which cleaning water stays, the water temperature rises and once eluted odors are volatilized again, so that the deodorizing ability decreases. . Furthermore, in the air circulation system, particularly when corrosive (acid-based) humidity gas or high dust gas is processed, water droplets may accumulate in the blower and corrode, or may cause high load and electric leakage, In addition, dust also adheres to the blade portion of the blower, causing a reduction in performance and failure.

総じて、上記三種の方式を各々単一に採用した場合は、十分な消臭能力を得ることができない。そこで、上記方式を併用した装置が一部実施されている。図2にその一例を示す。この装置の概略構成は、消臭液タンク15の上に吸着反応塔16、連結パイプ17及び消臭塔18を設けると共に、消臭液タンク15と消臭塔18の上部を循環パイプ19で接続している。尚。20はドレン、21は多孔板、22は充填剤、23は循環ポンプである。   In general, when each of the above three types is adopted singly, sufficient deodorizing ability cannot be obtained. In view of this, a part of the apparatus using the above method has been implemented. An example is shown in FIG. The schematic configuration of this apparatus is that an adsorption reaction tower 16, a connecting pipe 17 and a deodorizing tower 18 are provided on a deodorizing liquid tank 15, and an upper part of the deodorizing liquid tank 15 and the deodorizing tower 18 is connected by a circulation pipe 19. is doing. still. 20 is a drain, 21 is a perforated plate, 22 is a filler, and 23 is a circulation pump.

特開2003−326133号公報JP 2003-326133 A 特開2000−3257738号公報JP 2000-325738 A 特開2001−353419号公報JP 2001-353419 A

しかしながら、この種の脱臭装置では、生ゴミ発酵温度が50〜60℃という高温状態になることから、吸着反応塔16及び消臭塔18に流入する臭気ガスも高温となり、両塔16、18による吸着処理、洗浄処理の効率が低下する。また、両塔16、18においては、一般に反応容積や反応接触面積を増大させる必要があり、加えて臭気ガスの湿度が所定値以上に高くなると、消臭剤や消臭液の希釈化により脱臭効果が極端に低下するという問題があった。   However, in this type of deodorizing apparatus, the temperature of fermentation of raw garbage is 50 to 60 ° C., so that the odor gas flowing into the adsorption reaction tower 16 and the deodorizing tower 18 is also high. The efficiency of the adsorption process and the cleaning process decreases. In both towers 16 and 18, it is generally necessary to increase the reaction volume and reaction contact area. In addition, when the humidity of the odor gas becomes higher than a predetermined value, deodorization is performed by diluting the deodorant or deodorant liquid. There was a problem that the effect was extremely reduced.

また一般に、脱臭装置の開発において留意すべき事項としては、次の三点が挙げられる。
(1)臭気ガスの湿度(酸塩基性)による機器の損傷を防ぐこと。
(2)臭気ガスの送風能力を一定値以上に常時維持できること。
(3)処理塔内が負圧又は正圧のどちらにも偏らないこと。
In general, there are the following three points to be noted in the development of a deodorizing apparatus.
(1) Prevent equipment damage due to odor gas humidity (acid-basic).
(2) The ability to blow odor gas can be constantly maintained above a certain value.
(3) The inside of the treatment tower should not be biased to either negative pressure or positive pressure.

上記の留意事項を考慮して、本発明者は、臭気を洗浄する気泡槽等の洗浄塔と、臭気を吸着する吸着反応塔とを直列に接続する脱臭装置を鋭意研究してきた。ここで最も考慮すべきことは、臭気ガスに対する送風能力を低下させずに送風機等の機器類の損傷を防止することである。例えば、送風機に臭気ガス中の水分や塵埃が付着すると、送風機が早期に腐食したり損傷したりするだけでなく、洗浄塔などにおける脱臭効率を大幅に低下させる要因になる。
本発明は、上記のような課題に鑑みなされたものであり、その目的は、機器類の腐食や損傷を防止し、且つ洗浄部及び吸着部での脱臭効率を高めることができる洗浄吸着式脱臭装置を提供することにある。
In view of the above considerations, the inventor has intensively studied a deodorizing apparatus in which a cleaning tower such as a bubble tank for cleaning odor and an adsorption reaction tower for absorbing odor are connected in series. The most important thing to consider here is to prevent damage to equipment such as a blower without reducing the blowing capacity for odorous gas. For example, if moisture or dust in odor gas adheres to the blower, not only does the blower corrode or be damaged at an early stage, but it also causes a significant reduction in deodorization efficiency in a washing tower or the like.
The present invention has been made in view of the problems as described above, and its purpose is to prevent cleaning and adsorption deodorization capable of preventing corrosion and damage of equipment and improving deodorization efficiency in the cleaning unit and the adsorption unit. To provide an apparatus.

このため本発明の洗浄吸着式脱臭装置は、臭気ガスが通る経路に、臭気成分を洗浄水により洗浄除去する洗浄塔と、臭気成分を吸着剤により吸着除去する反応塔とを順次設け、前記洗浄塔と吸着反応塔との間に、前記洗浄塔内の臭気ガスを前記吸着反応塔側に吸引送風する送風機を配設したことを特徴とする。   For this reason, the cleaning adsorption deodorizing apparatus of the present invention is provided with a cleaning tower for cleaning and removing odorous components with cleaning water and a reaction tower for absorbing and removing odorous components with an adsorbent on the path through which the odorous gas passes. Between the tower and the adsorption reaction tower, a blower for sucking and blowing odor gas in the washing tower to the adsorption reaction tower side is provided.

本発明の洗浄吸着式脱臭装置は、臭気ガスが通る洗浄塔と吸着反応塔の間に、洗浄塔内の臭気ガスを吸着反応塔側に送る送風機を設けたので、水滴や粉塵による水溶性の腐食や損傷を防止することができ、併せて、洗浄塔や吸着反応塔における水溶性又は粒子状臭気の除去効率を大幅に高めることができるという優れた効果がある。   The cleaning adsorption deodorization apparatus of the present invention is provided with a blower for sending the odor gas in the cleaning tower to the adsorption reaction tower side between the cleaning tower through which the odor gas passes and the adsorption reaction tower. Corrosion and damage can be prevented, and at the same time, there is an excellent effect that the removal efficiency of water-soluble or particulate odor in the washing tower and the adsorption reaction tower can be greatly increased.

本発明の基本構成は、臭気ガスが通る経路に、洗浄塔及び吸着反応塔をガスの流れ方向に沿って直列に設ける。洗浄塔は、水、次亜塩素酸水溶液等により臭気を気液接触法で除去するものである。また、吸着反応塔は、活性炭、シリカゲル、ゼオライト、イオン交換樹脂などの吸着剤により臭気を除去するものである。この吸着反応塔と洗浄塔の間に吸引式送風機を設けることにより、洗浄塔内の滞留ガスを吸着反応塔側に所定の圧力で送風できるようにする。   In the basic configuration of the present invention, a cleaning tower and an adsorption reaction tower are provided in series along a gas flow direction in a path through which an odor gas passes. The washing tower is for removing odors with water, a hypochlorous acid aqueous solution or the like by a gas-liquid contact method. The adsorption reaction tower removes odors with an adsorbent such as activated carbon, silica gel, zeolite, or ion exchange resin. By providing a suction type blower between the adsorption reaction tower and the washing tower, the staying gas in the washing tower can be blown to the adsorption reaction tower side at a predetermined pressure.

洗浄塔には冷却器が設けられ、この冷却器により洗浄水の温度を最適範囲に制御する。洗浄水を所定以下の低温に調整したときは、臭気ガス中の水分や粉塵を洗浄除去できるだけでなく、臭気ガスの温度を低下させることが出来る。また、吸着反応塔内には活性炭が装填され、吸着反応塔の上部には、大気に通ずる排気口が形成される。   The washing tower is provided with a cooler, and the temperature of the wash water is controlled within the optimum range by this cooler. When the washing water is adjusted to a predetermined temperature or lower, not only can water and dust in the odor gas be washed away, but also the temperature of the odor gas can be lowered. Moreover, activated carbon is loaded in the adsorption reaction tower, and an exhaust port communicating with the atmosphere is formed in the upper part of the adsorption reaction tower.

洗浄塔において、ガスの湿度や温度を所定値以下に低下させると、吸着反応塔による吸着量が著しく増大すると共に、吸着表面への粉塵付着が激減して、臭気に対する吸着能力が大幅に向上する。また、本発明の洗浄塔では、洗浄水が絶えず流動するので、洗浄塔にて高温ガス(40〜70℃)を連続処理する場合でも、水温が40℃未満の低温状態に抑えられ、一旦溶出した臭気成分が再び揮発することはない。さらに、特に腐食性(酸塩基性)湿度ガス又は高粉塵ガスを処理する場合でも、送風機に水滴が溜まったり粉塵が付着することが抑制され、機器類に対する腐食や損傷のおそれがなくなる。   If the humidity and temperature of the gas are lowered below a predetermined value in the cleaning tower, the amount of adsorption by the adsorption reaction tower will increase significantly, and the dust adhesion to the adsorption surface will be drastically reduced and the adsorption capacity for odor will be greatly improved. . Further, in the washing tower of the present invention, since the washing water constantly flows, even when the hot gas (40 to 70 ° C.) is continuously processed in the washing tower, the water temperature is suppressed to a low temperature state of less than 40 ° C. and is once eluted. The odor component that has been removed does not volatilize again. Furthermore, even when a corrosive (acid-base) humidity gas or a high dust gas is treated, it is possible to prevent water droplets from accumulating and dust from being attached to the blower, thereby eliminating the risk of corrosion and damage to the equipment.

このように、本発明では、吸着反応塔と洗浄塔の間に送風機を配置したので、臭気ガスは送風機により洗浄塔内に強制吸引される。洗浄塔内に吸引されたガスは、吸着反応塔内の吸着部に送られ、ガスが吸着剤を通る際に残りの臭気成分が効果的に吸着される。   Thus, in this invention, since the air blower was arrange | positioned between the adsorption reaction tower and the washing | cleaning tower, odor gas is forcedly sucked in the washing tower by the air blower. The gas sucked into the washing tower is sent to the adsorption section in the adsorption reaction tower, and the remaining odor components are effectively adsorbed when the gas passes through the adsorbent.

ここで、送風機は洗浄塔の流出側に設けてあるので、ガス中の水分や塵埃が送風機の羽根表面などに付着することを防止できる。したがって、水分や塵埃により送風機に腐食や損傷を生ずるおそれがない。さらに、送風能力と送風圧力を適当範囲に増大させることができるので、線状塔や吸着反応塔での水溶性臭気や粒子状臭気の除去効率がアップする。   Here, since the blower is provided on the outflow side of the cleaning tower, moisture and dust in the gas can be prevented from adhering to the blade surface of the blower. Therefore, there is no possibility that the blower is corroded or damaged by moisture or dust. Furthermore, since the blowing capacity and the blowing pressure can be increased to an appropriate range, the removal efficiency of water-soluble odor and particulate odor in the linear tower and the adsorption reaction tower is improved.

以下に、本発明の実施の形態を図面に示す実施例に基づいて説明する。本実施例は、事業所又は家庭の生ゴミ処理器に本脱臭装置を連結し、生ゴミ処理器より発生する臭気ガスを洗浄吸着するものである。図1は本発明の一実施例に係る洗浄吸着式脱臭装置の処理フローを示す模式図、図2は従来装置の一例の概要を示す模式図である。   Hereinafter, embodiments of the present invention will be described based on examples shown in the drawings. In this embodiment, the deodorizing apparatus is connected to a garbage disposal device at an office or home, and the odor gas generated from the garbage disposal device is washed and adsorbed. FIG. 1 is a schematic diagram showing a processing flow of a cleaning adsorption deodorizing apparatus according to an embodiment of the present invention, and FIG. 2 is a schematic diagram showing an outline of an example of a conventional apparatus.

図1において、1は、処理時に臭気ガスが生じる生ゴミ処理器で、生ゴミ処理器1には一次パイプ2が連結されている。一次パイプ2の先端側は気泡槽(洗浄塔)3の上壁を貫通下降し、気泡槽3の底部に水平に延在している。パイプ2の先端部分はL字形の密閉管に形成され、その水平部分の管壁には多数の流出孔(図示せず)が穿設されている。気泡槽3は、臭気ガス中の臭気成分を洗浄除去するもので、内部には適当量の洗浄水4が貯留されている。この洗浄水4よりも上側の空間部はガス充満部5とされ、ガス充満部5には、洗浄処理後の臭気ガスが溜まるようになっている。気泡槽3の上面には、ガス充満部5内の臭気ガスを誘引するための二次パイプ6が連結され、二次パイプ6の先端側は吸着反応塔7の底面に連結されている。   In FIG. 1, reference numeral 1 denotes a garbage disposal device that generates odor gas during processing, and a primary pipe 2 is connected to the garbage disposal device 1. The tip end side of the primary pipe 2 penetrates and descends through the upper wall of the bubble tank (cleaning tower) 3 and extends horizontally at the bottom of the bubble tank 3. The distal end portion of the pipe 2 is formed as an L-shaped sealed tube, and a large number of outflow holes (not shown) are formed in the tube wall of the horizontal portion. The bubble tank 3 cleans and removes odorous components in the odorous gas, and stores an appropriate amount of cleaning water 4 inside. The space above the cleaning water 4 is a gas filling part 5, and the odor gas after the cleaning process is accumulated in the gas filling part 5. A secondary pipe 6 for attracting odorous gas in the gas filling unit 5 is connected to the upper surface of the bubble tank 3, and the tip side of the secondary pipe 6 is connected to the bottom surface of the adsorption reaction tower 7.

前記気泡槽3内には、洗浄水4の温度を検知する温度センサ8と、洗浄水4を冷却する冷却器9とが設けられている。温度センサ8及び冷却器9は、制御盤10に電気的に接続され、この制御盤10は、温度センサ8からの信号に基づいて、洗浄水4の温度を最適範囲内(40℃以下)に調整すべく冷却器10の運転を自動制御している。   In the bubble tank 3, a temperature sensor 8 that detects the temperature of the cleaning water 4 and a cooler 9 that cools the cleaning water 4 are provided. The temperature sensor 8 and the cooler 9 are electrically connected to a control panel 10, and the control panel 10 controls the temperature of the cleaning water 4 to be within an optimum range (40 ° C. or less) based on a signal from the temperature sensor 8. The operation of the cooler 10 is automatically controlled to be adjusted.

二次パイプ6における気泡槽3と吸着反応塔7の間には、送風機である吸引ファン11が設けられ、これにより、ガス充満部5内の充満ガスを吸引して、吸着反応塔7の下室に送給できるようになっている。吸着反応塔7は、臭気ガス中の臭気成分を物理化学的に除去するもので、多数の通気孔を持つ仕切板12により、ガス下室13と吸着上室14とに仕切られている。ガス下室13には、二次パイプ6を介して臭気ガスが流入し、ガス下室13内の流入ガスは、仕切板12の通気孔を介して、吸着上室14側に順次上昇するようになっている。吸着上室14内には吸着剤である活性炭が装填され、吸着上室14の上面には、大気に通じる排気口が形成されている。   A suction fan 11 as a blower is provided between the bubble tank 3 and the adsorption reaction tower 7 in the secondary pipe 6, thereby sucking the full gas in the gas filling section 5, below the adsorption reaction tower 7. It can be sent to the room. The adsorption reaction tower 7 physicochemically removes odor components in the odor gas, and is divided into a gas lower chamber 13 and an adsorption upper chamber 14 by a partition plate 12 having a large number of vent holes. Odor gas flows into the gas lower chamber 13 through the secondary pipe 6, and the inflow gas in the gas lower chamber 13 is sequentially raised to the adsorption upper chamber 14 side through the vent holes of the partition plate 12. It has become. Activated carbon as an adsorbent is loaded in the upper adsorption chamber 14, and an exhaust port communicating with the atmosphere is formed on the upper surface of the upper adsorption chamber 14.

次に、本実施例の作用を説明する。先ず、生ゴミ処理器1で生じた臭気ガスは、一次パイプ2を経て気泡槽3の底部に達し、一次パイプ2の流出孔から洗浄水4の中に放出される。そして、臭気ガスが洗浄水4中を浮上する際に、ガス中の臭気成分が洗浄除去される。すなわち、気泡槽3では、ガス入口(流出孔)より臭気ガスを曝気させることで、粒子性刺激物等の粉塵、及びアンモニア、低級アミン、低級脂肪酸等の水溶性臭気成分が高い効率で洗浄除去される。このときの洗浄水4の温度は、冷却器9により低温状態に調整されているため、ガスの溶解度が大きくなり、洗浄水4による洗浄脱臭が効果的に行われる。また、臭気ガスを冷却することにより、人間の嗅覚では感知され難くなる。   Next, the operation of this embodiment will be described. First, the odor gas generated in the garbage processor 1 reaches the bottom of the bubble tank 3 through the primary pipe 2 and is discharged into the wash water 4 from the outflow hole of the primary pipe 2. Then, when the odor gas rises in the cleaning water 4, the odor component in the gas is removed by washing. That is, in the bubble tank 3, the odorous gas is aerated from the gas inlet (outflow hole), so that dust such as particulate irritants and water-soluble odorous components such as ammonia, lower amines, and lower fatty acids are washed and removed with high efficiency. Is done. Since the temperature of the cleaning water 4 at this time is adjusted to a low temperature state by the cooler 9, the solubility of the gas is increased, and cleaning deodorization by the cleaning water 4 is effectively performed. In addition, by cooling the odor gas, it becomes difficult to be detected by human olfaction.

次いで、洗浄後の臭気ガスは、気泡荘3のガス充満部5に一旦溜まり、続いて吸引ファン11の作動により吸引される。すると、この吸引ガスは二次パイプ6を介して、吸着反応塔7のガス下室13内に流入する。流入後、ガス下室13内のガスは、仕切板12の通気孔を介して、吸着上室14内に順次移動して浮上する。そして、臭気ガスが吸着上室14内を浮上する際に、活性炭によりガス中の臭気成分が吸着除去される。この場合、活性炭による吸着脱臭は、低濃度の臭気ガスを処理するのに最適な吸着剤であり、また、気泡槽3により臭気ガス中の水分が除去されているため、活性炭による吸着効果が長期に渡って持続し、疎水性の臭気が効果的に除去される。   Next, the cleaned odor gas is temporarily accumulated in the gas filling portion 5 of the bubble bubble 3 and then sucked by the operation of the suction fan 11. Then, this suction gas flows into the gas lower chamber 13 of the adsorption reaction tower 7 through the secondary pipe 6. After the inflow, the gas in the gas lower chamber 13 sequentially moves into the adsorption upper chamber 14 and floats through the vent holes of the partition plate 12. When the odor gas rises in the adsorption upper chamber 14, the odor component in the gas is adsorbed and removed by the activated carbon. In this case, the adsorption deodorization with activated carbon is an optimal adsorbent for treating low-concentration odor gas, and the moisture in the odor gas is removed by the bubble tank 3, so that the adsorption effect by activated carbon is long-lasting. And the hydrophobic odor is effectively removed.

本発明に係る脱臭装置は、高温臭気、高湿度臭気、粉塵含有臭気に対して優れた消臭効果がある。例えば、高温臭気に対しては、気泡槽3で40℃以下に曝気冷却された臭気が活性炭内に流入するため、活性炭による消臭作用が最も効率良く発揮される。また、気泡槽3で40℃以下に曝気冷却された臭気が吸引ファン11に流入し、高温ガスが吸引ファン11を通過しないために、高温ガスによる吸引ファン11の損傷が防止される。   The deodorizing apparatus according to the present invention has an excellent deodorizing effect against high temperature odor, high humidity odor, and dust-containing odor. For example, for the high temperature odor, the odor aerated and cooled to 40 ° C. or lower in the bubble tank 3 flows into the activated carbon, so that the deodorizing action by the activated carbon is most effectively exhibited. Moreover, since the odor aerated and cooled to 40 ° C. or less in the bubble tank 3 flows into the suction fan 11 and the high temperature gas does not pass through the suction fan 11, damage to the suction fan 11 due to the high temperature gas is prevented.

一方、高湿度臭気に対しては、気泡槽3で曝気冷却されることにより、水分を除去して湿度が大幅に低下するため、活性炭による物理化学的な吸着処理が十分に発揮されるばかりでなく、高湿度ガスが吸引ファン11を通過しないために、高湿度ガス(強酸性湿度、強アルカリ性湿度)による吸引ファン11の損傷が防止される。さらに、粉塵を多く含んだ臭気に対しては、気泡槽3における洗浄作用により、粉塵は液中に溶出して確実に除去され、加えて、粉塵が吸引ファン11を通過しないために、粉塵による吸引ファン11の損傷が防止される。   On the other hand, for high-humidity odors, aeration and cooling in the bubble chamber 3 removes moisture and drastically reduces the humidity, so that the physicochemical adsorption treatment with activated carbon is fully exhibited. In addition, since the high-humidity gas does not pass through the suction fan 11, damage to the suction fan 11 due to the high-humidity gas (strong acid humidity, strong alkaline humidity) is prevented. Furthermore, for the odor containing a lot of dust, the dust is eluted and reliably removed by the cleaning action in the bubble tank 3, and in addition, the dust does not pass through the suction fan 11. Damage to the suction fan 11 is prevented.

このように、臭気ガス中の臭気成分は、洗浄作用と吸着作用により除去される。すなわち、先ず、気泡槽3の洗浄水4により、主に水溶性粒子状の臭気成分が除去され、次ぎに、吸着反応塔7の活性炭により、主に不溶性粒子状の臭気成分が除去される。この場合、吸引ファン11を通過する臭気ガスは、水溶性成分が除去された洗浄済みの低湿度(乾燥)ガスであり、このため吸引ファン11の表面には水分が殆ど付着しない。したがって、吸引ファン11が湿気により腐食するおそれがなくなる。また、吸引ファン11の表面には、水溶性粒子等の塵埃が殆ど付着しないので、吸引ファン11が塵埃により損傷することを防止できる。   Thus, the odor component in the odor gas is removed by the cleaning action and the adsorption action. That is, first, the water-soluble particulate odor component is mainly removed by the washing water 4 of the bubble tank 3, and then the insoluble particulate odor component is mainly removed by the activated carbon of the adsorption reaction tower 7. In this case, the odor gas passing through the suction fan 11 is a washed low humidity (dry) gas from which water-soluble components have been removed, and therefore, moisture hardly adheres to the surface of the suction fan 11. Therefore, there is no possibility that the suction fan 11 is corroded by moisture. Further, since dust such as water-soluble particles hardly adheres to the surface of the suction fan 11, it is possible to prevent the suction fan 11 from being damaged by dust.

要するに、気泡槽3と吸着反応塔7の間に吸引ファン11を配設したことにより、水分や塵埃による吸引ファン11の腐食や損傷をなくし、臭気ガスの送風機能を著しく向上させることができ、併せて送風機能の向上によって、気泡槽3と吸着反応塔7による脱臭効率をより一層増大させることができる。さらに吸着処理、洗浄処理の効率が高くなるので、反応容積や反応接触面積を増大させる必要がなく、設置スペースが縮小してコンパクト設計が可能になる。   In short, by disposing the suction fan 11 between the bubble tank 3 and the adsorption reaction tower 7, corrosion and damage of the suction fan 11 due to moisture and dust can be eliminated, and the function of blowing odor gas can be remarkably improved. In addition, the deodorizing efficiency by the bubble tank 3 and the adsorption reaction tower 7 can be further increased by improving the blowing function. Furthermore, since the efficiency of the adsorption treatment and the washing treatment is increased, it is not necessary to increase the reaction volume and the reaction contact area, and the installation space is reduced and a compact design is possible.

尚、本発明は上記実施例に限定されず、種々の応用変形例が可能である。例えば、上記実施例では、気泡槽3、吸着反応塔7及び吸引ファン11をそれぞれ単数としたが、これら構成要素3、7及び11は複数設置しても良く、複数設置する場合は、気泡槽3等を並列に接続することができる。   In addition, this invention is not limited to the said Example, A various application modification is possible. For example, in the above embodiment, the bubble tank 3, the adsorption reaction tower 7, and the suction fan 11 are each singular. However, a plurality of these constituent elements 3, 7, and 11 may be installed. 3 etc. can be connected in parallel.

本発明の一実施例に係る洗浄吸着式脱臭装置の処理フローを示す模式図である。It is a schematic diagram which shows the processing flow of the washing | cleaning adsorption type deodorizing apparatus which concerns on one Example of this invention. 従来の脱臭装置を示す模式図である。It is a schematic diagram which shows the conventional deodorizing apparatus.

符号の説明Explanation of symbols

1 生ゴミ処理器
2 一次パイプ
3 気泡槽(洗浄塔)
4 洗浄水
5 ガス充満部
6 二次パイプ
7 吸着反応塔
8 温度センサ
9 冷却器
10 制御盤
11 吸引ファン(送風機)
12 仕切板
13 ガス下室
14 吸着上室
15 消臭液タンク
16 吸着反応塔
17 連結パイプ
18 消臭塔
19 循環パイプ
20 ドレン
21 多孔板
22 充填剤
23 循環ポンプ
1 Garbage Disposer 2 Primary Pipe 3 Bubble Tank (Washing Tower)
4 Washing Water 5 Gas Filling Section 6 Secondary Pipe 7 Adsorption Reaction Tower 8 Temperature Sensor 9 Cooler 10 Control Panel 11 Suction Fan (Blower)
12 Partition plate 13 Gas lower chamber 14 Adsorption upper chamber 15 Deodorant liquid tank 16 Adsorption reaction tower 17 Connection pipe 18 Deodorization tower 19 Circulation pipe 20 Drain 21 Porous plate 22 Filler 23 Circulation pump

Claims (1)

臭気ガスが通る経路に、臭気成分を洗浄水により洗浄除去する洗浄塔と、臭気成分を吸着剤により吸着除去する吸着反応塔とを順次設け、前記洗浄塔と吸着反応塔の間に、前記洗浄塔内の臭気ガスを前記吸着反応塔側に吸引送風する送風機を配設したことを特徴とする洗浄吸着式脱臭装置。 A washing tower for washing and removing odor components with washing water and an adsorption reaction tower for adsorbing and removing odor components with an adsorbent are sequentially provided in a path through which the odor gas passes, and the washing is performed between the washing tower and the adsorption reaction tower. A cleaning adsorption deodorizing apparatus comprising a blower for sucking and blowing odor gas in the tower toward the adsorption reaction tower.
JP2004224048A 2004-07-30 2004-07-30 Washing/adsorption type deodorizer Pending JP2006043498A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2004224048A JP2006043498A (en) 2004-07-30 2004-07-30 Washing/adsorption type deodorizer

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2004224048A JP2006043498A (en) 2004-07-30 2004-07-30 Washing/adsorption type deodorizer

Publications (1)

Publication Number Publication Date
JP2006043498A true JP2006043498A (en) 2006-02-16

Family

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP2004224048A Pending JP2006043498A (en) 2004-07-30 2004-07-30 Washing/adsorption type deodorizer

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Country Link
JP (1) JP2006043498A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010029832A (en) * 2008-07-31 2010-02-12 System Kikou Co Ltd Treatment method of volatile component-containing air, and treatment apparatus of volatile component-containing air
CN108499342A (en) * 2018-03-23 2018-09-07 登封特卡电子科技有限公司 A kind of intelligence emission-control equipment
CN115608112A (en) * 2022-11-22 2023-01-17 广东捷玛节能科技股份有限公司 Based on flue gas CO 2 Purification regeneration energy-saving process

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010029832A (en) * 2008-07-31 2010-02-12 System Kikou Co Ltd Treatment method of volatile component-containing air, and treatment apparatus of volatile component-containing air
CN108499342A (en) * 2018-03-23 2018-09-07 登封特卡电子科技有限公司 A kind of intelligence emission-control equipment
CN115608112A (en) * 2022-11-22 2023-01-17 广东捷玛节能科技股份有限公司 Based on flue gas CO 2 Purification regeneration energy-saving process

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