JP2012011288A - Deodorizing device - Google Patents

Deodorizing device Download PDF

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JP2012011288A
JP2012011288A JP2010148407A JP2010148407A JP2012011288A JP 2012011288 A JP2012011288 A JP 2012011288A JP 2010148407 A JP2010148407 A JP 2010148407A JP 2010148407 A JP2010148407 A JP 2010148407A JP 2012011288 A JP2012011288 A JP 2012011288A
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biological
carrier
deodorizing
fiber
deodorization
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Akinori Kawachi
昭典 河内
Kazutomi Sugawara
一臣 菅原
Takao Taruya
隆雄 樽谷
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Unitika Ltd
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    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
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Abstract

PROBLEM TO BE SOLVED: To efficiently remove malodor components contained in malodorous gas.SOLUTION: A deodorizing device is a device for deodorizing gas containing malodor components. The deodorizing device includes a deodorization tower filled with a carrier for biological deodorization. The deodorization tower is installed on the upper stage of an aeration tank side wall or on the upper stage of a passage part between aeration tanks. The carrier for biological deodorization is a fiber bundle comprising activated carbon fibers and thermoplastic synthetic fiber and has a bulk density of 0.05-0.15 g/cm, a porosity of 70-98%, a maximum cross section diameter of 5-25 mm, and a length of 5-30 mm.

Description

本発明は脱臭装置に関し、たとえば、ばっ気槽から大量に発生する硫化水素、メチルメルカプタン、硫化メチル、二硫化メチル、アンモニア、有機酸などを含有した悪臭ガスのための脱臭装置に関する。   The present invention relates to a deodorizing apparatus, for example, a deodorizing apparatus for malodorous gas containing hydrogen sulfide, methyl mercaptan, methyl sulfide, methyl disulfide, ammonia, organic acid and the like generated in large quantities from an aeration tank.

従来より下水処理場の大きな問題点の一つは、周辺住民からの悪臭の苦情である。そのため、各下水処理場においては、臭気の強い最初沈殿池などを覆蓋し、発生した悪臭ガスを臭気ダクトにより1ヶ所に集め、薬液洗浄法、活性炭吸着法や生物脱臭法を利用した脱臭装置で悪臭成分を除去した後、脱臭ファンから大気中に放出している。   One of the major problems of sewage treatment plants has been complaints of bad odors from neighboring residents. Therefore, in each sewage treatment plant, the first settling basin with strong odor is covered, and the generated bad odor gas is collected in one place by the odor duct, and the deodorization equipment using chemical cleaning method, activated carbon adsorption method or biological deodorization method is used. After removing malodorous components, they are released from the deodorizing fan into the atmosphere.

このうち、生物脱臭法は、臭気成分を栄養源として繁殖する微生物を接触材の表面に担持させ、この微生物により臭気成分を分解、脱臭する方法であり、これらの接触材としては、土壌、腐植土、プラスチック、セラミックやその加工品、およびそれらに微生物を固着させたものが使用されている(特許文献1、2、3)。   Among them, the biological deodorization method is a method in which microorganisms that propagate using odor components as nutrient sources are supported on the surface of the contact material, and the odor components are decomposed and deodorized by the microorganisms. Soil, plastic, ceramic and processed products thereof, and those in which microorganisms are fixed are used (Patent Documents 1, 2, and 3).

特開平10−137536号公報JP-A-10-137536 特開2002−336639号公報Japanese Patent Application Laid-Open No. 2002-336639 特開平8−10557号公報JP-A-8-10557

しかし、脱臭性能を高めるためには、ガスとの接触表面積が大きく、処理効率が高い密な生物脱臭用担体を使用する必要があるため、ガス通過の際の圧力損失が大きくなる。また、脱臭装置に充填する生物脱臭用担体が粗な場合には、ガス通過の際の圧力損失は低く、脱臭装置をたとえばばっ気槽に設置する場合は槽内への吹き込み空気圧を利用して容易に通過させることが可能である。しかしながら、かかる場合は、ガスとの接触面積が小さいため、担体すなわち接触材と接触できずに脱臭処理されなかったガスが多量に大気中に放出される。これを防止するためには、脱臭塔を大規模なものとしてガスとの接触の機会を多くするなどの対策が必要である。   However, in order to improve the deodorizing performance, it is necessary to use a dense biological deodorizing carrier having a large contact surface area with the gas and high processing efficiency, so that the pressure loss during gas passage increases. In addition, when the biological deodorizing carrier filled in the deodorizing device is rough, the pressure loss during gas passage is low, and when the deodorizing device is installed in an aeration tank, for example, the air pressure blown into the tank is used. It can be easily passed. However, in such a case, since the contact area with the gas is small, a large amount of gas that cannot be contacted with the carrier, that is, the contact material and has not been deodorized is released into the atmosphere. In order to prevent this, it is necessary to take measures such as making the deodorization tower large and increasing the chance of contact with gas.

本発明は、ばっ気槽などから発生するガスに含有される悪臭成分を、効率的に除去できるようにすることを目的とする。   An object of the present invention is to enable efficient removal of malodorous components contained in gas generated from an aeration tank or the like.

本発明者らが、上記の課題を解決するために鋭意検討し、到達した発明の要旨は、悪臭成分を含有したガスを脱臭するための装置であって、生物脱臭用担体を充填した生物脱臭塔を備え、この生物脱臭塔はばっ気槽側壁の上段あるいはばっ気槽間の通路部の上段に設けられ、前記生物脱臭用担体は、活性炭素繊維と熱可塑性合成繊維とを含む繊維収束体であって、嵩密度0.05〜0.15g/cm、空隙率70〜98%、断面の最大直径5〜25mm、長さ5〜30mmであることを特徴とする脱臭装置である。 The inventors of the present invention diligently studied to solve the above-mentioned problems, and the summary of the achieved invention is an apparatus for deodorizing a gas containing a malodorous component, which is a biological deodorization packed with a biological deodorizing carrier. The biological deodorization tower is provided at the upper stage of the side wall of the aeration tank or the upper stage of the passage part between the aeration tanks, and the biological deodorization carrier is a fiber converging body including activated carbon fibers and thermoplastic synthetic fibers. The deodorizing apparatus is characterized by having a bulk density of 0.05 to 0.15 g / cm 3 , a porosity of 70 to 98%, a maximum cross-sectional diameter of 5 to 25 mm, and a length of 5 to 30 mm.

本発明によると、活性炭素繊維製の充填材を微生物担体として使用することにより、吸着効果を併用した微生物による生物脱臭効果を得ることができ、このため効率的な脱臭が可能となり、悪臭ガスを、高速かつ安い運転コストで高効率に処理できるのみならず、その担体が、活性炭素繊維と熱可塑性合成繊維とを含む繊維収束体であって、嵩密度0.05〜0.15g/cm、空隙率70〜98%であるため、圧力損失の少ない状態で効率よく脱臭を行うことができる。 According to the present invention, by using a filler made of activated carbon fiber as a microbial carrier, it is possible to obtain a biological deodorizing effect due to microorganisms combined with an adsorption effect, which enables efficient deodorization and prevents malodorous gas from In addition to high-speed and low-cost operation costs, the carrier is a fiber converging body containing activated carbon fibers and thermoplastic synthetic fibers, and has a bulk density of 0.05 to 0.15 g / cm 3. Further, since the porosity is 70 to 98%, deodorization can be efficiently performed in a state where the pressure loss is small.

さらに、本発明によると、生物脱臭塔がばっ気槽側壁の上段あるいはばっ気槽間の通路部の上段に設けられているため、生物脱臭塔の重量による耐荷重の問題を防止することができる。また、生物脱臭塔への臭気ダクトも非常に短いものとなるため、被処理ガスが臭気ダクト中を流れる間の温度変化もほとんどなく、脱臭性能が良好な状態に維持することができる。   Furthermore, according to the present invention, since the biological deodorization tower is provided on the upper stage of the side wall of the aeration tank or the upper stage of the passage part between the aeration tanks, it is possible to prevent the problem of load resistance due to the weight of the biological deodorization tower. . Further, since the odor duct to the biological deodorization tower is very short, there is almost no temperature change while the gas to be treated flows through the odor duct, and the deodorization performance can be maintained in a good state.

生物脱臭塔およびその周辺部の一例の一部切欠斜視図である。It is a partially cutaway perspective view of an example of a biological deodorization tower and its peripheral part. 図1の生物脱臭塔を備えた脱臭装置の例を示す概略図である。It is the schematic which shows the example of the deodorizing apparatus provided with the biological deodorizing tower of FIG.

以下、本発明について詳細に説明する。
本発明において、生物脱臭塔に充填されて微生物を固定化する接触材としては、活性炭素繊維と熱可塑性合成繊維とを主成分とする成形体を用いる必要がある。本発明で使用する活性炭素繊維は、石炭ピッチ、石油ピッチ、レーヨン、フェノール、アクリル、ビニロン系材料あるいはセルロース系材料等を原料とし、通常の方法で不融、賦活処理して微細孔を形成したもので、比表面積がBET法による測定値で500m/g以上のものが好ましい。比表面積が500m/g未満であると、細孔が小さくなり臭気成分との接触が困難となる。
Hereinafter, the present invention will be described in detail.
In the present invention, it is necessary to use a molded body mainly composed of activated carbon fibers and thermoplastic synthetic fibers as a contact material that is packed in a biological deodorization tower and immobilizes microorganisms. The activated carbon fiber used in the present invention is made of coal pitch, petroleum pitch, rayon, phenol, acrylic, vinylon-based material or cellulosic material, etc., and is infusible and activated by ordinary methods to form fine pores. The specific surface area is preferably 500 m 2 / g or more as measured by the BET method. When the specific surface area is less than 500 m 2 / g, the pores become small and contact with the odor component becomes difficult.

この接触材は、活性炭素繊維と熱可塑性合成繊維と混合して複数本の繊維束を形成した繊維収束体の形態とされる。
活性炭素繊維とともに充填材を構成する熱可塑性合成繊維としては、たとえば、ポリエステル、ナイロン、ポリエチレン、ポリプロピレン、共重合ポリエステルなどからなる単成分繊維、あるいは、芯部にポリエステルを用いるとともに、鞘部にポリエチレン、ポリプロピレン、共重合ポリエステルなどを用いた芯鞘型複合繊維などがある。
This contact material is in the form of a fiber converging body in which activated carbon fibers and thermoplastic synthetic fibers are mixed to form a plurality of fiber bundles.
As the thermoplastic synthetic fiber constituting the filler together with the activated carbon fiber, for example, a single component fiber made of polyester, nylon, polyethylene, polypropylene, copolymerized polyester, or the like, or polyester for the core and polyethylene for the sheath Core-sheath type composite fibers using polypropylene, copolyester and the like.

活性炭素繊維と熱可塑性合成繊維との混合質量比は、90:10〜10:90、特に85:15〜15:85の範囲が好ましい。活性炭素繊維の割合が大きすぎると、構造体あるいは充填材の成形性が悪くなり、逆に少なすぎると臭気成分との接触が悪くなる。   The mixing mass ratio of the activated carbon fiber and the thermoplastic synthetic fiber is preferably in the range of 90:10 to 10:90, particularly 85:15 to 15:85. If the ratio of the activated carbon fiber is too large, the moldability of the structure or the filler is deteriorated, and conversely if it is too small, the contact with the odor component is deteriorated.

本発明で用いられる繊維収束体は、活性炭素繊維を開繊・混合した後、繊維束を形成させ、この繊維束を熱処理して熱可塑性合成繊維により繊維間を接着して棒状に形成し、次いで、任意の長さに切断することにより得ることができる。   The fiber converging body used in the present invention, after opening and mixing the activated carbon fiber, to form a fiber bundle, heat-treating this fiber bundle and bonding between the fibers with a thermoplastic synthetic fiber to form a rod, Subsequently, it can obtain by cutting to arbitrary length.

棒状の繊維収束体の大きさは、断面の最大直径が5〜25mmであることが必要であり、8〜20mmの範囲が好ましい。また、棒状の繊維収束体の断面が円状、楕円状、ドーナツ状、トリローバル状、十字形状、星形状等のものが、取り扱いやすく、生物脱臭用担体として適している。なお、ここにいう最大直径とは、球状、ドーナツ状の場合は直径、楕円状の場合は長軸の長さ、その他の形状の場合はその最大長さを意味するものである。棒状の繊維収束体の長さは、5〜30mmであることが必要であり、10〜20mmの範囲が好ましい。   As for the size of the rod-like fiber converging body, the maximum diameter of the cross section is required to be 5 to 25 mm, and the range of 8 to 20 mm is preferable. In addition, a rod-shaped fiber converging body having a circular, elliptical, donut-shaped, trilobal, cross-shaped or star-shaped cross section is easy to handle and suitable as a biological deodorizing carrier. The maximum diameter here means the diameter in the case of a spherical shape or a donut shape, the length of the major axis in the case of an ellipse shape, and the maximum length in the case of other shapes. The length of the rod-like fiber converging body needs to be 5 to 30 mm, and preferably in the range of 10 to 20 mm.

最大直径と長さが上記の範囲を超えて大き過ぎると、ガス通過の際の圧力損失は低いが、ガスとの接触面積が小さいため、処理効率は低下する。逆に棒状の繊維収束体が上記の範囲を超えて小さ過ぎると、ガス通過の際の圧力損失が大きく、たとえばばっ気槽における吹き込み空気圧を利用した自然通風は困難となる。   If the maximum diameter and length are too large beyond the above range, the pressure loss during the passage of gas is low, but the processing efficiency decreases because the contact area with the gas is small. On the other hand, if the rod-like fiber converging body is too small beyond the above range, the pressure loss at the time of gas passage is large, and for example, natural ventilation using the blowing air pressure in the aeration tank becomes difficult.

本発明において、繊維収束体の嵩密度は0.05〜0.15g/cmであることが必要である。嵩密度が0.15g/cmよりも大きいと、この繊維収束体にて形成される担体が密になり過ぎ、空隙率が低下して微生物の付着容量が減少し、処理効率が低下する結果となる。さらに装置重量も重くなり、装置設置場所の制限を受けるため、実用性が低下する。反対に嵩密度が0.05g/cmよりも小さいと、被処理ガスとの接触効率が低下し、処理効率の大きな低下につながる。このため嵩密度は0.05〜0.085g/cmの範囲が好ましい。 In the present invention, the bulk density of the fiber converging body needs to be 0.05 to 0.15 g / cm 3 . When the bulk density is larger than 0.15 g / cm 3, the carrier formed by the fiber converging body becomes too dense, the porosity is lowered, the adhesion capacity of microorganisms is reduced, and the processing efficiency is lowered. It becomes. Furthermore, the weight of the apparatus becomes heavier, and the practicality of the apparatus is lowered because the apparatus is limited in place. On the other hand, when the bulk density is less than 0.05 g / cm 3 , the contact efficiency with the gas to be processed decreases, leading to a large decrease in processing efficiency. For this reason, the bulk density is preferably in the range of 0.05 to 0.085 g / cm 3 .

棒状の繊維収束体の空隙率は70〜98%であることが必要である。この空隙率は、通気性や強度のほか、水分保持量にも関連性があり、空隙率が98%より大きい場合は、繊維収束体にて形成される担体が脆くなるため、高く積むと下部の担体が潰れる可能性があり、実用性が低下する。空隙率が70%より小さいと、通気性が不良となるのに加え、水分保持量も少なくなり、散水停止の影響が脱臭性能に大きな影響を及ぼす。このため、80〜95%の範囲が好ましい。   The porosity of the rod-like fiber converging body needs to be 70 to 98%. This porosity is related not only to air permeability and strength but also to the amount of water retained. When the porosity is greater than 98%, the carrier formed by the fiber converging body becomes brittle. The carrier may be crushed and the practicality is reduced. When the porosity is less than 70%, in addition to poor air permeability, the amount of water retained is also reduced, and the influence of watering stop greatly affects the deodorization performance. For this reason, the range of 80 to 95% is preferable.

図1は、生物脱臭塔およびその周辺部の一例を示す図である。図1において、生物脱臭塔1には、生物脱臭用担体が充填された充填層2が配設されており、充填層2の上方には散水器3が、充填層2の下方には受水槽4が配設されている。受水槽4の上部における空間の部分には悪臭ガス導入口5が連通されており、受水槽4の底部には、散水器3からの散水にもとづき充填層2から流下した水を排出するための排水口6が連通されている。散水器3よりも上方の位置には、排気口7が設けられている。充填層2は、上下方向および並列に複数配列させてもよく、3段以上の複数段とすることもできる。   FIG. 1 is a diagram illustrating an example of a biological deodorization tower and its peripheral part. In FIG. 1, a biological deodorization tower 1 is provided with a packed bed 2 filled with a biological deodorizing carrier, a sprinkler 3 above the packed bed 2, and a water receiving tank below the packed bed 2. 4 is arranged. The malodorous gas inlet 5 is communicated with the space in the upper part of the water receiving tank 4, and the bottom of the water receiving tank 4 is used for discharging water flowing down from the packed bed 2 based on the water sprayed from the water sprinkler 3. A drain port 6 is communicated. An exhaust port 7 is provided at a position above the sprinkler 3. A plurality of packed layers 2 may be arranged in the vertical direction and in parallel, or may be a plurality of three or more stages.

上記の構成によると、生物脱臭用担体を充填した充填層2の上方に散水器3を配設して連続的または間欠的に散水することにより、担体の表面が湿潤状態に保持され、微生物の付着と繁殖が促進されるとともに、酸化生成物が洗浄除去される。間欠的に散水する場合には、散水間隔は、0.5〜4時間に1回程度が適当であり、一回当たりの散水時間は、散水器3の形状及び吐出水量により異なるが、0.2〜15分が適当である。なお、充填層2が複数の場合は、各充填層2ごとに散水器3を配設してもよく、あるいは一つの散水器3ですべての充填層2に散水するようにしてもよい。   According to said structure, the surface of the support | carrier is hold | maintained in a moist state by arrange | positioning the water sprinkler 3 above the packed bed 2 filled with the biological deodorizing support | carrier, and spraying water continuously or intermittently. Adhesion and propagation are promoted and oxidation products are washed away. In the case of intermittent watering, it is appropriate that the watering interval is about once every 0.5 to 4 hours, and the watering time per time varies depending on the shape of the watering device 3 and the amount of discharged water. 2 to 15 minutes is appropriate. In addition, when there are a plurality of packed beds 2, a sprinkler 3 may be arranged for each packed bed 2, or all packed beds 2 may be sprinkled with one sprinkler 3.

脱臭の効果は、臭気成分の種類と濃度によって異なるが、悪臭ガスの通気速度(LV)と空塔速度(SV)とによって決定される。本発明の脱臭装置によれば、上述のように、担体を構成する繊維収束体の嵩密度が0.01〜0.10g/cmであるとともにその空隙率70〜98%であることにもとづき、悪臭ガス通過速度(LV)が0.4m/s以下のときに、生物脱臭塔内の圧力損失を15mmHO以下とすることができる。 The effect of deodorization varies depending on the type and concentration of the odor component, but is determined by the bad odor gas ventilation rate (LV) and the superficial velocity (SV). According to the deodorizing apparatus of the present invention, as described above, the bulk density of the fiber converging body constituting the carrier is 0.01 to 0.10 g / cm 3 and its porosity is 70 to 98%. When the malodorous gas passage speed (LV) is 0.4 m / s or less, the pressure loss in the biological deodorization tower can be 15 mmH 2 O or less.

上述のように、生物脱臭用担体を充填した生物脱臭塔を、ばっ気槽側壁の上段あるいはばっ気槽間の通路部の上段に設けた本発明の脱臭装置は、このばっ気槽への吹き込み空気を利用した自然通風だけで良好に脱臭させることができる。空塔速度は、2000h-1以下であれば、良好な処理を行うことができる。 As described above, the deodorizing apparatus of the present invention in which the biological deodorizing tower filled with the biological deodorizing carrier is provided in the upper stage of the side wall of the aeration tank or the upper stage of the passage part between the aeration tanks is blown into the aeration tank. It can be deodorized satisfactorily only by natural ventilation using air. If the superficial velocity is 2000 h −1 or less, good treatment can be performed.

また、生物脱臭塔の生物脱臭用担体は繊維製であるため、比表面積が大きく臭気物質との接触効率がよく、さらに、通気性が優れており、そのため上記のように圧力損失が非常に小さいため、ファンを用いて通風させる場合にも低動力のファンにて運転することができる。また、生物脱臭用担体は、活性炭素繊維と熱可塑性合成繊維とを含むものであり、空隙率が大きく軽量にできる。そのため、たとえば図1における充填層2を1段で2000mm程度積層しても、圧密化することなく良好な処理が可能である。   Moreover, since the carrier for biological deodorization of the biological deodorization tower is made of fiber, the specific surface area is large, the contact efficiency with the odorous substance is good, and the air permeability is excellent, so that the pressure loss is very small as described above. Therefore, even when a fan is used for ventilation, it can be operated with a low-power fan. In addition, the biological deodorizing carrier includes activated carbon fibers and thermoplastic synthetic fibers, and has a large porosity and can be reduced in weight. Therefore, for example, even if the packing layer 2 in FIG.

図2は、生物脱臭塔1を備えた脱臭装置の具体例を示す図である。図2においては、ばっ気槽11、11、…が直列に複数ステージ設けられている。12は各ばっ気槽11の側壁であり、隣り合うばっ気槽11、11の側壁12、12どうしの間には通路13が形成されている。14はばっ気槽11の覆蓋、15はばっ気のためのブロワ、16はばっ気槽11における散気装置である。ばっ気槽11、11、…を直列に複数ステージ設けて処理を行う場合には、特に最初のステージで悪臭が発生しやすい。このため覆蓋14は、第1ステージと第2ステージとのばっ気槽11、11にのみ設けられている。   FIG. 2 is a diagram illustrating a specific example of a deodorization apparatus including the biological deodorization tower 1. In FIG. 2, a plurality of aeration tanks 11, 11,... Are provided in series. Reference numeral 12 denotes a side wall of each aeration tank 11, and a passage 13 is formed between the side walls 12, 12 of the adjacent aeration tanks 11, 11. 14 is a cover for the aeration tank 11, 15 is a blower for aeration, and 16 is an air diffuser in the aeration tank 11. When processing is performed by providing a plurality of aeration tanks 11, 11,... In series, bad odor is likely to occur particularly in the first stage. For this reason, the cover 14 is provided only in the aeration tanks 11 and 11 of the first stage and the second stage.

生物脱臭塔1は、隣り合う第1ステージと第2ステージのばっ気槽11、11の側壁12、12の上段どうしの間に跨るようにして配置されており、すなわち通路13の上方に設けられており、その重量は側壁12、12によって支持されている。   The biological deodorization tower 1 is arranged so as to straddle between the upper stages of the side walls 12 and 12 of the aeration tanks 11 and 11 of the adjacent first stage and second stage, that is, provided above the passage 13. Its weight is supported by the side walls 12, 12.

このような構成において、ばっ気槽7にて発生した悪臭成分を含有する被処理ガス17は、散気装置12からの吹き込み空気18の圧力を利用して生物脱臭塔1に導入され、その内部で脱臭処理され、図1に示す排気口7から大気中に放出される。   In such a configuration, the gas to be treated 17 containing malodorous components generated in the aeration tank 7 is introduced into the biological deodorization tower 1 using the pressure of the blown air 18 from the air diffuser 12, and the inside thereof Is deodorized and discharged from the exhaust port 7 shown in FIG.

上記のように生物脱臭塔1は、ばっ気槽11、11の側壁12、12の上段どうしの間に跨って設けられており、その重量は側壁12、12によって支持されているため、耐荷重の面での問題とはならない。また、生物脱臭塔1への臭気ダクトも非常に短いものとなるため、被処理ガス17が臭気ダクト中を流れる間の温度変化もほとんどなく、脱臭性能が良好な状態に維持される。   As described above, the biological deodorization tower 1 is provided between the upper stages of the side walls 12 and 12 of the aeration tanks 11 and 11, and the weight is supported by the side walls 12 and 12. This is not a problem. Further, since the odor duct to the biological deodorization tower 1 is very short, there is almost no temperature change while the gas 17 to be treated flows through the odor duct, and the deodorization performance is maintained in a good state.

上記に代えて、生物脱臭塔1は、一つのばっ気槽11の側壁12の上段のみに設けることもできる。このようなものであると、単数のばっ気槽しか有しない下水処理場などにも生物脱臭塔1を設置することができる。   Instead of the above, the biological deodorization tower 1 can be provided only on the upper stage of the side wall 12 of one aeration tank 11. In such a case, the biological deodorization tower 1 can be installed in a sewage treatment plant having only a single aeration tank.

以下に本発明の実施例・比較例を示す。
(実施例1)
比表面積1000m/gのピッチ系繊維状活性炭20質量%と、芯鞘型ポリエステル未延伸繊維80質量%とをカーディングマシンで開繊、混合し、1mあたり6gのカードスライバーとした。このカードスライバーを熱処理したのち切断し、最大直径8mm、長さ10mmの六葉柱状繊維収束体を得て、生物脱臭用担体とした。この生物脱臭用担体の嵩密度は0.085g/cm、その空隙率は92%であった。
Examples and Comparative Examples of the present invention are shown below.
Example 1
20% by mass of pitch-type fibrous activated carbon having a specific surface area of 1000 m 2 / g and 80% by mass of core-sheath polyester unstretched fiber were opened and mixed with a carding machine to obtain a card sliver of 6 g per meter. This card sliver was heat-treated and then cut to obtain a six-leaf post-like fiber converging body having a maximum diameter of 8 mm and a length of 10 mm, which was used as a biological deodorizing carrier. This biological deodorizing carrier had a bulk density of 0.085 g / cm 3 and a porosity of 92%.

上記の生物脱臭用担体へ微生物を植種した後、該生物脱臭用担体を生物脱臭塔1中の充填層2に充填し、図1に示されるような生物脱臭塔を得た。この生物脱臭塔を、図2に示すようにばっ気槽間の通路部の上段に設け、脱臭装置を得た。   After inoculating microorganisms on the biological deodorizing carrier, the biological deodorizing carrier was filled in the packed bed 2 in the biological deodorizing tower 1 to obtain a biological deodorizing tower as shown in FIG. This biological deodorization tower was provided in the upper stage of the passage part between the aeration tanks as shown in FIG. 2 to obtain a deodorization apparatus.

図2に記載されたばっ気槽における吹き込み空気18の圧力を利用して、悪臭を有する被処理ガス17を生物脱臭塔1の内部における充填層2よりも下部に導入し、処理後に大気中に放出した。そのときの各種の硫黄化合物の濃度は、ガスクロマトグラフ法にて分析した。表1にその運転条件を示し、表2にその処理結果を示すが、処理結果は非常に良好であった。   Using the pressure of the blown air 18 in the aeration tank shown in FIG. 2, a gas to be treated 17 having a bad odor is introduced below the packed bed 2 inside the biological deodorizing tower 1 and is put into the atmosphere after the treatment. Released. The concentration of various sulfur compounds at that time was analyzed by gas chromatography. Table 1 shows the operating conditions, and Table 2 shows the processing results. The processing results were very good.

Figure 2012011288
Figure 2012011288

Figure 2012011288
(実施例2)
比表面積1300m/gのピッチ系繊維状活性炭25質量%と、芯鞘型ポリエステル未延伸繊維75質量%とをカーディングマシンで開繊、混合し、1mあたり6gのカードスライバーとした。このカードスライバーを熱処理したのち切断し、最大直径8mm、長さ10mmの六葉柱状繊維収束体を得て、生物脱臭用担体とした。この生物脱臭用担体の嵩密度は0.090g/cm、その空隙率は92%であった。
Figure 2012011288
(Example 2)
25% by mass of pitch-based fibrous activated carbon having a specific surface area of 1300 m 2 / g and 75% by mass of core-sheath polyester unstretched fiber were opened and mixed with a carding machine to obtain a card sliver of 6 g per meter. This card sliver was heat-treated and then cut to obtain a six-leaf post-like fiber converging body having a maximum diameter of 8 mm and a length of 10 mm, which was used as a biological deodorizing carrier. This biological deodorizing carrier had a bulk density of 0.090 g / cm 3 and a porosity of 92%.

上記で得られた六葉柱状繊維収束体からなる生物脱臭用担体を使用して、実施例1と同様に生物脱臭塔を得、この生物脱臭塔を用いた脱臭装置により悪臭ガスを処理した。運転条件は、実施例1と同じにした。表2にその処理結果を示すが、処理結果は非常に良好であった。
(比較例1)
芯鞘型ポリエステル未延伸繊維100質量%の繊維をカーディングマシンで開繊、混合し、1mあたり6gのカードスライバーとした。そして、このカードスライバーから製造した最大直径8mm、長さ8mmの六葉柱状繊維収束体を得て、生物脱臭用担体とした。この生物脱臭用担体の嵩密度は0.105g/cm、その空隙率は92%であった。
Using the biological deodorizing carrier composed of the six-leaf columnar fiber converging body obtained above, a biological deodorizing tower was obtained in the same manner as in Example 1, and malodorous gas was treated by a deodorizing apparatus using this biological deodorizing tower. The operating conditions were the same as in Example 1. The processing results are shown in Table 2, and the processing results were very good.
(Comparative Example 1)
A fiber of 100% by mass of the core-sheath polyester unstretched fiber was opened and mixed with a carding machine to obtain a card sliver of 6 g per meter. Then, a six-leaf columnar fiber converging body having a maximum diameter of 8 mm and a length of 8 mm produced from this card sliver was obtained and used as a biological deodorizing carrier. This biological deodorizing carrier had a bulk density of 0.105 g / cm 3 and a porosity of 92%.

上記で得られた六葉柱状繊維収束体からなる生物脱臭用担体を使用して、実施例1と同様に生物脱臭塔を得、この生物脱臭塔を用いた脱臭装置により被処理ガスを処理した。運転条件は、実施例1と同じにした。表2にその処理結果を示すが、活性炭素繊維が用いられていなかったため、処理結果は実施例1、2のものに比べて劣っていた。
(比較例2)
芯鞘型ポリエステル未延伸繊維100質量%の繊維をカーディングマシンで開繊、混合し、1mあたり6gのカードスライバーとした。そして、このカードスライバーから製造した最大直径25mm、長さ25mmの六葉柱状繊維収束体を得て、生物脱臭用担体とした。この生物脱臭用担体の嵩密度は0.04g/cm、その空隙率は95%であった。
Using the biological deodorization carrier comprising the six-leaf columnar fiber converging body obtained above, a biological deodorization tower was obtained in the same manner as in Example 1, and the gas to be treated was treated by a deodorization apparatus using this biological deodorization tower. . The operating conditions were the same as in Example 1. Although the treatment result is shown in Table 2, since the activated carbon fiber was not used, the treatment result was inferior to those of Examples 1 and 2.
(Comparative Example 2)
A fiber of 100% by mass of the core-sheath polyester unstretched fiber was opened and mixed with a carding machine to obtain a card sliver of 6 g per meter. Then, a six-leaf pillar-shaped fiber converging body having a maximum diameter of 25 mm and a length of 25 mm produced from this card sliver was obtained and used as a biological deodorizing carrier. This biological deodorization carrier had a bulk density of 0.04 g / cm 3 and a porosity of 95%.

上記で得られた六葉柱状繊維収束体からなる生物脱臭用担体を使用して、実施例1と同様に生物脱臭塔を得、この生物脱臭塔を用いた脱臭装置により被処理ガスを処理した。運転条件は、実施例1と同じにした。表2にその処理結果を示すが、活性炭素繊維が用いられておらず、嵩密度が低かったため、処理結果は実施例1、2のものに比べて劣っていた。
(比較例3)
実施例1のものと同じカードスライバーを熱処理したのち切断し、外径25mm、長さ25mmの六葉柱状繊維収束体を得て、生物脱臭用担体とした。この生物脱臭用担体の嵩密度は0.035g/cm、その空隙率は96%であった。
Using the biological deodorization carrier comprising the six-leaf columnar fiber converging body obtained above, a biological deodorization tower was obtained in the same manner as in Example 1, and the gas to be treated was treated by a deodorization apparatus using this biological deodorization tower. . The operating conditions were the same as in Example 1. Although the treatment result is shown in Table 2, since the activated carbon fiber was not used and the bulk density was low, the treatment result was inferior to those of Examples 1 and 2.
(Comparative Example 3)
The same card sliver as in Example 1 was heat-treated and then cut to obtain a six-leaf post-like fiber converging body having an outer diameter of 25 mm and a length of 25 mm, which was used as a biological deodorizing carrier. This biological deodorizing carrier had a bulk density of 0.035 g / cm 3 and a porosity of 96%.

上記で得られた六葉柱状繊維収束体からなる生物脱臭用担体を使用して、実施例1と同様に生物脱臭塔を得、この生物脱臭塔を用いた脱臭装置により被処理ガスを処理した。運転条件は、実施例1と同じにした。表2にその処理結果を示すが、嵩密度が低かったため、処理結果は実施例1、2のものに比べて劣っていた。   Using the biological deodorization carrier comprising the six-leaf columnar fiber converging body obtained above, a biological deodorization tower was obtained in the same manner as in Example 1, and the gas to be treated was treated by a deodorization apparatus using this biological deodorization tower. . The operating conditions were the same as in Example 1. The processing results are shown in Table 2. Since the bulk density was low, the processing results were inferior to those of Examples 1 and 2.

1 生物脱臭塔
2 充填層
3 散水器
4 受水槽
5 悪臭ガス導入口
6 排水口
7 排気口
11 ばっ気槽
12 側壁
13 通路
14 ばっ気槽11の覆蓋
15 ばっ気のためのブロワ
16 ばっ気槽11における散気装置
17 被処理ガス
18 吹き込み空気
DESCRIPTION OF SYMBOLS 1 Biological deodorization tower 2 Packing layer 3 Sprinkler 4 Water receiving tank 5 Odor gas introduction port 6 Drainage port 7 Exhaust port 11 Aeration tank 12 Side wall 13 Passage 14 Cover of aeration tank 11 15 Blower for aeration 16 Aeration tank Air diffuser in 11 17 Gas to be treated 18 Blowing air

Claims (1)

悪臭成分を含有したガスを脱臭するための装置であって、生物脱臭用担体を充填した生物脱臭塔を備え、この生物脱臭塔はばっ気槽側壁の上段あるいはばっ気槽間の通路部の上段に設けられ、前記生物脱臭用担体は、活性炭素繊維と熱可塑性合成繊維とを含む繊維収束体であって、嵩密度0.05〜0.15g/cm、空隙率70〜98%、断面の最大直径5〜25mm、長さ5〜30mmであることを特徴とする脱臭装置。 An apparatus for deodorizing a gas containing malodorous components, comprising a biological deodorization tower filled with a biological deodorization carrier, and this biological deodorization tower is located at the upper stage of the side wall of the aeration tank or the upper stage of the passage between the aeration tanks. The biological deodorizing carrier is a fiber converging body containing activated carbon fibers and thermoplastic synthetic fibers, and has a bulk density of 0.05 to 0.15 g / cm 3 , a porosity of 70 to 98%, and a cross section. The maximum deodorizing device has a diameter of 5 to 25 mm and a length of 5 to 30 mm.
JP2010148407A 2010-06-30 2010-06-30 Deodorizing device Pending JP2012011288A (en)

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0833884A (en) * 1994-07-25 1996-02-06 Mitsubishi Kakoki Kaisha Ltd Waste water treating device installed with deodorizer
JP2000237530A (en) * 1999-02-18 2000-09-05 Sekine:Kk Medium for gas treatment using fiber assembly and gas treatment apparatus using the same
JP2003033625A (en) * 2001-07-24 2003-02-04 Seikow Chemical Engineering & Machinery Ltd Biological deodorizing method
JP2003210931A (en) * 2002-01-22 2003-07-29 Unitika Ltd Method for deodorization treatment
JP2005218993A (en) * 2004-02-06 2005-08-18 Unitika Ltd Microorganism treatment carrier for ultrapure water production
JP2006247440A (en) * 2005-03-08 2006-09-21 Unitika Ltd Deodorizing device

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0833884A (en) * 1994-07-25 1996-02-06 Mitsubishi Kakoki Kaisha Ltd Waste water treating device installed with deodorizer
JP2000237530A (en) * 1999-02-18 2000-09-05 Sekine:Kk Medium for gas treatment using fiber assembly and gas treatment apparatus using the same
JP2003033625A (en) * 2001-07-24 2003-02-04 Seikow Chemical Engineering & Machinery Ltd Biological deodorizing method
JP2003210931A (en) * 2002-01-22 2003-07-29 Unitika Ltd Method for deodorization treatment
JP2005218993A (en) * 2004-02-06 2005-08-18 Unitika Ltd Microorganism treatment carrier for ultrapure water production
JP2006247440A (en) * 2005-03-08 2006-09-21 Unitika Ltd Deodorizing device

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