JP2005238112A - Deodorization method and apparatus for odor gas - Google Patents

Deodorization method and apparatus for odor gas Download PDF

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JP2005238112A
JP2005238112A JP2004051692A JP2004051692A JP2005238112A JP 2005238112 A JP2005238112 A JP 2005238112A JP 2004051692 A JP2004051692 A JP 2004051692A JP 2004051692 A JP2004051692 A JP 2004051692A JP 2005238112 A JP2005238112 A JP 2005238112A
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gas
odor
metal phthalocyanine
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Kazuomi Hondo
和臣 本藤
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Sumitomo Heavy Industries Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a deodorization method for an odor gas capable of exhibiting excellent deodorization effect even if the concentration of an odor component of the odor gas generated from a sewage treatment facility or the like is remarkably varied, reducing an operation cost and maintaining excellent treatment performance for a long period of time, and an apparatus. <P>SOLUTION: The odor gas generated from the sewage treatment facility or the like is deodorized by previously removing hydrogen sulfide or the like by organisms deodorization using a microorganism immobilization carrier and contacting the organisms treatment gas with a metal phthalocyanine catalyst-containing solution. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は、下水処理場、し尿処理場及び食品工場や化学工場などから発生するガス中の不快な臭気成分を効率よく除去することができる臭気ガスの脱臭方法及び装置に関する。   The present invention relates to a method and apparatus for deodorizing odor gas that can efficiently remove unpleasant odor components in gas generated from sewage treatment plants, human waste treatment plants, food factories, chemical factories, and the like.

下水、し尿などの処理施設及び各種工場などから発生する臭気ガスは生活環境の改善要求が高まり、その対策が求められている。特に下水処理場等で発生する臭気ガスには、臭気成分として、硫化水素が比較的多く含まれ、その他にメチルメルカプタン、硫化メチル、二硫化メチルなどの硫黄系臭気成分や、アンモニア等の塩基性ガスが含まれているため、これらの臭気成分を除去する必要がある。
これらの臭気成分を含む臭気ガスの脱臭方法としては、薬液洗浄法、活性炭吸着法、生物脱臭法、オゾン酸化法、プラズマ触媒酸化法など各種のものが知られている。
Odor gas generated from treatment facilities such as sewage and human waste and various factories has been increasingly demanded to improve the living environment, and countermeasures have been demanded. Odor gas generated in sewage treatment plants in particular contains a relatively large amount of hydrogen sulfide as an odor component. In addition, sulfur-based odor components such as methyl mercaptan, methyl sulfide, and methyl disulfide, and basic substances such as ammonia. Since gas is contained, it is necessary to remove these odor components.
Various methods such as a chemical solution cleaning method, an activated carbon adsorption method, a biological deodorization method, an ozone oxidation method, and a plasma catalyst oxidation method are known as methods for deodorizing odor gas containing these odor components.

しかし、薬液洗浄法は薬品費が高いことと廃液処理を要するという問題がある。活性炭吸着法では吸着量に限界があり、吸着能が低下した時点で、新しいものに交換するか、厄介な再生を行う必要がある。特に活性炭吸着法では、水分の多いガスを処理する場合、水分の吸着により臭気成分の吸着量が著しく低下する。
オゾン酸化法やプラズマ酸化法でも、低温で処理する場合、処理するガス中の水分によって金属酸化物等の固体触媒の性能が低下するという問題があり、また、オゾンやプラズマの発生装置が高価であり、電力消費も大きいといった問題点を有している。
However, the chemical cleaning method has a problem that the chemical cost is high and waste liquid treatment is required. In the activated carbon adsorption method, the amount of adsorption is limited, and when the adsorption capacity is lowered, it is necessary to replace it with a new one or perform troublesome regeneration. In particular, in the activated carbon adsorption method, when a gas with a large amount of water is processed, the adsorption amount of the odor component is significantly reduced due to the adsorption of moisture.
Even in the ozone oxidation method and the plasma oxidation method, when the treatment is performed at a low temperature, there is a problem that the performance of the solid catalyst such as a metal oxide is deteriorated due to the moisture in the gas to be treated, and the ozone and plasma generator are expensive. There is a problem that power consumption is large.

最近では生物脱臭法の一つである充填塔式生物脱臭法が多く用いられている。充填塔式生物脱臭法は、充填塔内に設けられた生物担体充填層(以下、単に充填層と記す)に臭気ガスを通すことにより臭気ガス中の臭気成分を分解除去する方法である。
ところが、充填塔式生物脱臭法は、一般にランニングコストが安く、硫化水素のような易分解性の臭気成分は除去しやすいものの、硫化メチル、二硫化メチルなどの難分解性の臭気成分は除去しにくい。また極端な臭気濃度の変動には追随することができない。このため、充填塔式生物脱臭装置の後段にオゾン共存下で固体触媒を充填した触媒反応器を設ける方法が提案されている(例えば、特許文献1参照)。
Recently, a packed tower type biological deodorization method, which is one of the biological deodorization methods, has been widely used. The packed tower type biological deodorization method is a method of decomposing and removing odor components in odor gas by passing odor gas through a biological carrier packed bed (hereinafter simply referred to as packed bed) provided in the packed tower.
However, the packed tower type biological deodorization method is generally low in running cost and easy to remove easily decomposable odor components such as hydrogen sulfide, but removes hardly degradable odor components such as methyl sulfide and methyl disulfide. Hateful. Moreover, it cannot follow the fluctuation | variation of an extreme odor density | concentration. For this reason, a method of providing a catalytic reactor filled with a solid catalyst in the coexistence of ozone in the subsequent stage of a packed tower type biological deodorization apparatus has been proposed (for example, see Patent Document 1).

しかし、この方法では固体触媒に水分が吸着したり、硫黄や硫酸等が付着して触媒が劣化し、性能が低下してしまうという問題を有している。
また、その他の脱臭法として、遷移金属キレート化合物を臭気成分の酸化触媒として使用する方法が知られている。遷移金属キレート化合物としては、遷移金属ポルフィリン誘導体が有効であり、特に金属フタロシアニンが適している。
However, this method has a problem in that moisture is adsorbed on the solid catalyst or sulfur, sulfuric acid or the like adheres to the catalyst, resulting in deterioration of the performance.
As another deodorization method, a method using a transition metal chelate compound as an oxidation catalyst for an odor component is known. As the transition metal chelate compound, a transition metal porphyrin derivative is effective, and metal phthalocyanine is particularly suitable.

例えば、金属フタロシアニンを化学繊維に担持させた脱臭材や金属フタロシアニンを担持させた不織布と活性炭フィルタ等を併用した消臭フィルタを利用した方法が提案されている(例えば、特許文献2、特許文献3、特許文献4参照)。 For example, a method using a deodorizing material in which metal phthalocyanine is supported on a chemical fiber or a deodorizing filter in which a nonwoven fabric in which metal phthalocyanine is supported and an activated carbon filter is used in combination has been proposed (for example, Patent Document 2 and Patent Document 3). , See Patent Document 4).

金属フタロシアニンは室温等の低温でも触媒機能を有しているが、触媒活性が小さいため、消臭速度が遅く、消臭効果が十分でないという問題を有している。また、臭気成分の分解や酸化によって生ずる硫黄や硫酸等の付着により活性が低下するという問題を有している。
さらに、従来のこれらの方法では、金属フタロシアニンを繊維等に含浸担持させたものを乾燥させて調整するので、製作に時間とコストがかかるという問題もある。
Metal phthalocyanine has a catalytic function even at a low temperature such as room temperature, but has a problem that its deodorizing rate is slow and its deodorizing effect is not sufficient because its catalytic activity is small. In addition, there is a problem that the activity decreases due to adhesion of sulfur, sulfuric acid, etc. caused by decomposition and oxidation of odor components.
Further, in these conventional methods, since the metal phthalocyanine impregnated and supported on the fiber is dried and adjusted, there is a problem that it takes time and cost to manufacture.

特開2000−246050号公報JP 2000-246050 A 特開昭62−6985号公報JP-A 62-6985 特開昭62−6986号公報JP-A-62-2986 特開平11−9671号公報JP-A-11-9671

本発明は上記のような事情に鑑みてなされたものであり、その目的は、下水処理施設等から発生する臭気ガスの臭気成分を、その濃度が著しく変動する場合であっても優れた脱臭効果を発揮すると共に、運転コストを低減し得、長期間に亘って優れた処理性能を維持することが可能な臭気ガスの脱臭方法及びそのような機能を有する脱臭装置を提供することである。   The present invention has been made in view of the circumstances as described above, and its purpose is to provide an excellent deodorizing effect even when the concentration of the odor component of odor gas generated from a sewage treatment facility or the like varies significantly. It is to provide a deodorizing method of odor gas and a deodorizing apparatus having such a function, which can reduce the operating cost and can maintain excellent processing performance for a long period of time.

本発明は、上述した課題を達成するためになされたもので、以下の手段で解決された。
下水処理設備等から発生する臭気ガスの脱臭方法であって、臭気ガスを予め微生物固定化担体を用いて生物脱臭し、その生物脱臭処理ガスを更に、金属フタロシアニン触媒含有溶液(以下、単に金属フタロシアニン溶液と記す)と接触させて脱臭するようにした。
使用した前記金属フタロシアニン溶液に蓄積するイオウ等の固形物を固液分離により除去して循環使用することも特徴とする。
The present invention has been made to achieve the above-described problems, and has been solved by the following means.
A method for deodorizing odorous gas generated from a sewage treatment facility or the like, wherein the odorous gas is biologically deodorized in advance using a microorganism-immobilized carrier, and the biological deodorized gas is further added to a metal phthalocyanine catalyst-containing solution (hereinafter simply referred to as metal phthalocyanine). Deodorized by contacting with a solution).
It is also characterized in that solid substances such as sulfur accumulated in the used metal phthalocyanine solution are removed by solid-liquid separation and recycled.

下水処理施設等から発生する臭気ガスを脱臭する装置であって、臭気ガスを生物処理する微生物固定化担体を充填した生物脱臭塔を前段に設置し、その生物脱臭処理ガスを更に処理する金属フタロシアニン溶液を散布する気液接触反応塔(以下、単に反応塔と記す)を後段に設置した。
前記反応塔で使用された金属フタロシアニン溶液より固形物を取り除く固液分離装置を前記反応塔に備えることも特徴とする。
Metal phthalocyanine that deodorizes odorous gas generated from sewage treatment facilities, etc., and is equipped with a biological deodorization tower filled with a microorganism-immobilized carrier for biologically treating odorous gas, and further processes the biological deodorized gas A gas-liquid contact reaction tower (hereinafter simply referred to as a reaction tower) for spraying the solution was installed in the subsequent stage.
The reaction tower is also provided with a solid-liquid separation device that removes solids from the metal phthalocyanine solution used in the reaction tower.

予め生物脱臭により硫化水素を除去し、その処理ガス中の未分解の臭気成分を金属フタロシアニン溶液で処理する本発明の脱臭方法及び装置を使用することによって、下水処理施設等から発生するガス中の臭気成分を十分に除去することができる。
また、経済的且つ長期間に亘って効率よく安定して処理することが可能である。特に、臭気濃度が高い場合、また、臭気濃度の変動が大きい場合でも安定した脱臭処理が可能である。
By using the deodorizing method and apparatus of the present invention that removes hydrogen sulfide in advance by biological deodorization and treats the undecomposed odorous component in the treated gas with a metal phthalocyanine solution, Odor components can be sufficiently removed.
Further, it is possible to perform the treatment efficiently and stably over a long period of time. In particular, stable deodorization treatment is possible even when the odor concentration is high or when the fluctuation of the odor concentration is large.

以下、本発明の実施の形態について説明するが、本発明は下記の実施の形態になんら限定されるものではなく、適宜変更して実施することが可能なものである。
図1は本発明による臭気ガスの脱臭方法を実施する装置の構成例を示す概略図である。図1に示すように、脱臭装置20は、例えば下水処理設備から発生する臭気ガスを脱臭するものであり、臭気ガスは、臭気成分として、例えば硫化水素、メチルメルカプタン、硫化メチル、二硫化メチル、アンモニア等を含む。
Hereinafter, embodiments of the present invention will be described, but the present invention is not limited to the following embodiments, and can be implemented with appropriate modifications.
FIG. 1 is a schematic view showing a configuration example of an apparatus for carrying out the odor gas deodorizing method according to the present invention. As shown in FIG. 1, the deodorization apparatus 20 deodorizes the odor gas which generate | occur | produces, for example from a sewage treatment facility, and an odor gas is an odor component, for example, hydrogen sulfide, methyl mercaptan, methyl sulfide, methyl disulfide, Including ammonia.

脱臭装置20は、その臭気ガスを生物脱臭処理する生物脱臭塔1と、金属フタロシアニン溶液が上部より散布される反応塔2を備えている。生物脱臭塔1の下部から臭気ガスである被処理ガスが配管100を介して供給され、生物脱臭塔1の内部に配置されている充填層3を通り、生物脱臭塔1の上部より配管101を介して排出される。
充填層3には微生物を付着させるセラミックスやプラスチック等の担体が充填されている。
The deodorization apparatus 20 includes a biological deodorization tower 1 that biologically deodorizes the odor gas, and a reaction tower 2 in which a metal phthalocyanine solution is sprayed from above. A gas to be treated, which is an odor gas, is supplied from the lower part of the biological deodorization tower 1 through the pipe 100, passes through the packed bed 3 disposed inside the biological deodorization tower 1, and passes through the pipe 101 from the upper part of the biological deodorization tower 1. Is discharged through.
The packed layer 3 is filled with a carrier such as ceramic or plastic to which microorganisms adhere.

充填層3には散水管4によって活性汚泥処理水等が供給され、これによって臭気成分を分解する微生物が増殖するようになっている。被処理ガスはこの充填層3を通されるので、被処理ガス中の臭気成分が微生物によって分解され脱臭される。
この生物脱臭塔1では、通常硫化水素は約99%、メチルメルカプタンは約90%、硫化メチル及び二硫化メチルは約70〜80%、アンモニアは約50%が除去される。中でも硫化水素については効率よく除去することができる。
Activated sludge treated water or the like is supplied to the packed bed 3 through the water spray pipe 4 so that microorganisms that decompose the odorous component grow. Since the gas to be treated is passed through the packed bed 3, the odor components in the gas to be treated are decomposed and deodorized by microorganisms.
In this biological deodorization tower 1, about 99% of hydrogen sulfide, about 90% of methyl mercaptan, about 70 to 80% of methyl sulfide and methyl disulfide, and about 50% of ammonia are removed. Among these, hydrogen sulfide can be efficiently removed.

なお、充填層3に散水される活性汚泥処理水等は活性汚泥処理水槽5から、ポンプ6によって散水配管L1を通して散水管4に導かれる。また、生物脱臭塔1の底部は、充填層3から落下する散水を溜める水溜部7となっており、水溜部7の溜水は微生物にとって最適なpHになるように調整され、水溜部7の溜水も充填層3の散水としてポンプ8によって散水配管L2を通して汲み上げられ、散水管4より充填層3に散水される。散水は充填層3の洗浄も兼ねて使用される。 In addition, the activated sludge treated water sprayed to the packed bed 3 is led from the activated sludge treated water tank 5 to the sprinkling pipe 4 by the pump 6 through the sprinkling pipe L1. Further, the bottom of the biological deodorization tower 1 is a water reservoir 7 for storing water sprinkled from the packed bed 3, and the water stored in the water reservoir 7 is adjusted so as to have an optimum pH for microorganisms. The stored water is also pumped up through the sprinkling pipe L <b> 2 by the pump 8 as sprinkling of the packed bed 3, and sprinkled into the packed bed 3 through the sprinkled pipe 4. The water spray is also used for cleaning the packed bed 3.

なお、生物脱臭塔1において、充填層3を1層のみ使用する形態を説明したが、充填層3を2層以上、あるいは生物脱臭塔1を2塔以上設けることも可能であり、また、各充填層3の上方にそれぞれ散水管4を設けることも可能である。 In the biological deodorization tower 1, only one packed bed 3 is described. However, it is possible to provide two or more packed beds 3 or two or more biological deodorizing towers 1, It is also possible to provide a water spray pipe 4 above the packed bed 3.

生物脱臭塔1で硫化水素を効率よく取り除かれた処理ガスは、金属フタロシアニン溶液9がポンプ11によって汲み上げられ、配管L3及び散水管10を介して上部より散布される反応塔2の下部に配管101を介して導入される。反応塔2の内部には充填層12が配置されている。充填層12には気液接触を効果的に行うためにセラミックスやプラスチックス製等の充填材が充填されている。   The processing gas from which hydrogen sulfide has been efficiently removed in the biological deodorization tower 1 is pumped with a metal phthalocyanine solution 9 by a pump 11 and is sprinkled from the top through a pipe L3 and a sprinkling pipe 10 to the lower part of the reaction tower 2 with a pipe 101. Is introduced through. A packed bed 12 is disposed inside the reaction tower 2. The filling layer 12 is filled with a filler such as ceramics or plastics for effective gas-liquid contact.

充填層12内で、臭気ガスは金属フタロシアニン溶液9との接触により、ガス中の臭気成分は液中の金属フタロシアニンの触媒作用により酸素と反応し、分解あるいは酸化される。
例えば生物脱臭塔1で分解されずに残存する硫化水素は硫黄や硫酸に変換され、溶液中に捕捉される。またメチルメルカプタンは二硫化メチル等の無臭あるいは臭気の低いガスに酸化される。同様に、その他の硫化物も金属フタロシアニンの触媒作用により無臭あるいは臭気の低いガスに酸化される。
反応塔2を通過した処理ガスは配管102を介して大気へ排出される。なお、更に高度な処理を行う場合には、反応塔2の後段に小型の活性炭吸着塔(図示していない)などを設けて処理した後、大気へ放出することもできる。
In the packed bed 12, the odor gas reacts with oxygen by contact with the metal phthalocyanine solution 9 and the odor component in the gas is catalyzed by metal phthalocyanine in the liquid, and is decomposed or oxidized.
For example, hydrogen sulfide remaining without being decomposed in the biological deodorization tower 1 is converted into sulfur or sulfuric acid and captured in the solution. Methyl mercaptan is oxidized to odorless or low-odor gas such as methyl disulfide. Similarly, other sulfides are oxidized to odorless or low odor gas by the catalytic action of metal phthalocyanine.
The processing gas that has passed through the reaction tower 2 is discharged to the atmosphere via the pipe 102. In addition, when performing a further advanced process, after processing by providing a small activated carbon adsorption tower (not shown) etc. in the back | latter stage of the reaction tower 2, it can also discharge | release to air | atmosphere.

生物脱臭塔1の処理ガスは水分がほぼ飽和状態であり、水分含有量が多く、通常の固体触媒では水分吸着により、触媒活性が大幅に低下するが、金属フタロシアニンは水溶液系の触媒であるため水分の影響を受けない。また、前段の生物脱臭塔1で大部分の硫化水素が予め取り除かれているため反応塔2で生成する硫黄が少ない。そのため金属フタロシアニン溶液9の汚染が抑制されるので、長期間安定した性能を維持することが可能である。   The treatment gas of the biological deodorization tower 1 is almost saturated with water, has a high moisture content, and the catalytic activity of a normal solid catalyst is greatly reduced due to moisture adsorption. However, metal phthalocyanine is an aqueous catalyst. Not affected by moisture. In addition, since most of the hydrogen sulfide is removed in advance in the biological deodorization tower 1 in the previous stage, the amount of sulfur generated in the reaction tower 2 is small. Therefore, since the contamination of the metal phthalocyanine solution 9 is suppressed, it is possible to maintain stable performance for a long time.

長期間の装置の運転によって、硫黄の生成、蓄積が生じた場合には、金属フタロシアニン溶液の汚染による性能の低下や反応塔2内の散水管10等の閉塞問題を防止するために、金属フタロシアニン溶液9をポンプ13及び配管L4を介して沈殿分離、ろ過分離または膜分離などの固液分離装置14に供給して、硫黄を取り除き、配管L5を介して反応塔2へ戻される。   When sulfur has been generated or accumulated due to long-term operation of the apparatus, metal phthalocyanine is used to prevent performance degradation due to contamination of the metal phthalocyanine solution and clogging problems such as the sprinkling pipe 10 in the reaction tower 2. The solution 9 is supplied to a solid-liquid separation device 14 such as precipitation separation, filtration separation or membrane separation via a pump 13 and a pipe L4, sulfur is removed, and the solution 9 is returned to the reaction tower 2 via a pipe L5.

固液分離装置14では、被処理ガス中から吸収液に捕り込まれ粉塵等も取り除かれる。
また、硫酸等の生成、吸収によって吸収液が著しく酸性化した場合には、水酸化ナトリウム溶液等のアルカリ剤を金属フタロシアニン溶液9へ添加して適正なpHに調整される。適したpHは使用する金属フタロシアニンの種類によって異なるが、通常pH4〜10程度である。
In the solid-liquid separator 14, dust and the like are removed from the gas to be treated by being trapped in the absorbing liquid.
Further, when the absorbing solution is remarkably acidified due to the generation and absorption of sulfuric acid or the like, an alkaline agent such as a sodium hydroxide solution is added to the metal phthalocyanine solution 9 to adjust to an appropriate pH. A suitable pH varies depending on the type of metal phthalocyanine used, but is usually about pH 4-10.

以上の通り、本発明では、生物脱臭塔1において、後段の反応塔2に悪影響を及ぼす硫化水素が予め取り除かれていること、また、生物脱臭処理ガスが高含水であっても、水溶液に安定な触媒を使用しているので、水分や硫酸等の影響が少なく、また、生成する固体硫黄等も容易に取り除くことが可能なため、安定して高い性能を長期間維持することができる。 As described above, in the present invention, in the biological deodorization tower 1, hydrogen sulfide that adversely affects the subsequent reaction tower 2 is removed in advance, and even if the biological deodorization treatment gas has a high water content, it is stable in an aqueous solution. Since a simple catalyst is used, there is little influence of moisture, sulfuric acid, etc., and solid sulfur and the like that can be generated can be easily removed, so that stable and high performance can be maintained for a long period of time.

また、後段の反応塔2を設置することにより、臭気成分の効率的な除去が可能になるばかりでなく、前段の生物脱臭塔1を小型化することが可能である。逆に前段に生物脱臭塔1を設置することにより、後段の反応塔2内で使用される高価なフタロシアニン触媒の使用量を低減することが可能である。
ここで、反応塔2の形式としては、反応塔2内にセラミックスやプラスチック等を充填した充填層12を設けることなく、上部の散水管10よりスプレーノズル等で液体を噴霧する形式など各種のものを使用することが可能である。
Further, by installing the reaction tower 2 at the rear stage, not only the odorous components can be efficiently removed, but also the biological deodorization tower 1 at the front stage can be downsized. Conversely, by installing the biological deodorization tower 1 in the former stage, it is possible to reduce the amount of expensive phthalocyanine catalyst used in the latter reaction tower 2.
Here, as the form of the reaction tower 2, there are various kinds such as a form in which a liquid is sprayed from the upper watering pipe 10 with a spray nozzle or the like without providing the packed bed 12 filled with ceramics or plastic in the reaction tower 2. Can be used.

また、反応塔2に使用される金属フタロシアニン触媒は、図2に示されるような構造式をもつもので、構造式中のXは水素または置換基を、Mは配位金属を示す。置換基Xとしては、例えば、カルボキシル基、スルホン酸基、アミン塩類、第4級アンモニウム基など各種のものが使用でき、1種類の基には限られず各々別な基が置換されたものでもよい。なかでも、カルボキシル基、アミノ基、第4級アンモニウム基などのアニオン性基あるいはカチオン性基が2〜8程度置換されているものが好ましい。   Further, the metal phthalocyanine catalyst used in the reaction tower 2 has a structural formula as shown in FIG. 2, wherein X in the structural formula represents hydrogen or a substituent, and M represents a coordination metal. Examples of the substituent X include various groups such as a carboxyl group, a sulfonic acid group, an amine salt, and a quaternary ammonium group. The substituent X is not limited to one type, and may be a group in which different groups are substituted. . Especially, what substituted about 2-8 about anionic groups or cationic groups, such as a carboxyl group, an amino group, and a quaternary ammonium group, is preferable.

また、配位金属MはFe、Co、Mn、V、Cuなどのものが使用できる。これらの金属フタロシアニンを中性、酸生あるいはアルカリ性の水に溶解させ、または懸濁させた状態で使用する。その濃度は通常、0.1〜10%程度に成るように調整される。例えば、金属フタロシアニンとして、オクタカルボキシフタロシアニン鉄を使用する場合には、水酸化ナトリウムの希アルカリ性溶液に0.5〜5%程度になるように溶解した後、硫酸等の酸でpH8〜10程度に調整して使用することができる。
なお、金属フタロシアニンは安定なので、金属フタロシアニン溶液の酸化力をより高めるために、次亜塩素酸ナトリウム等の酸化剤を添加して使用することもできる。
Further, the coordination metal M may be Fe, Co, Mn, V, Cu or the like. These metal phthalocyanines are used dissolved or suspended in neutral, acid or alkaline water. The concentration is usually adjusted to be about 0.1 to 10%. For example, when octacarboxyphthalocyanine iron is used as the metal phthalocyanine, it is dissolved in a dilute alkaline solution of sodium hydroxide so as to be about 0.5 to 5%, and then adjusted to pH 8 to 10 with an acid such as sulfuric acid. Can be used with adjustment.
Since metal phthalocyanine is stable, an oxidizing agent such as sodium hypochlorite can be added and used in order to further enhance the oxidizing power of the metal phthalocyanine solution.

また、本発明では、臭気濃度の低い通常時は生物脱臭塔1の運転のみを行い、その処理ガスを大気へ放出し、汚泥の流入、汚泥の搬送、攪拌時などの臭気の高くなる時にのみ、生物脱臭塔1の処理ガスを更に反応塔2で処理するようにしてもよい。   Further, in the present invention, only when the odor concentration is low, only the biological deodorization tower 1 is operated, and the treatment gas is released into the atmosphere, and only when the odor becomes high, such as during sludge inflow, sludge transport, and stirring. The processing gas in the biological deodorization tower 1 may be further processed in the reaction tower 2.

本発明に係わる脱臭装置の構成例を示す概略図である。It is the schematic which shows the structural example of the deodorizing apparatus concerning this invention. 金属フタロシアニンの構造式を示す図である。It is a figure which shows the structural formula of metal phthalocyanine.

符号の説明Explanation of symbols

1 生物脱臭塔
2 反応塔
3 充填層
4 散水管
5 活性汚泥処理水槽
6、8、11、13 ポンプ
7 水溜部
9 金属フタロシアニン溶液
10 散水管
12 充填層
14 固液分離装置
DESCRIPTION OF SYMBOLS 1 Biological deodorizing tower 2 Reaction tower 3 Packing bed 4 Sprinkling pipe 5 Activated sludge treatment water tank 6, 8, 11, 13 Pump 7 Water reservoir
9 Metal phthalocyanine solution
10 watering pipe 12 packed bed 14 solid-liquid separator

Claims (4)

臭気ガスを予め微生物固定化担体を用いて生物脱臭し、その生物脱臭処理ガスを更に、金属フタロシアニン触媒含有溶液と接触させて処理を行うことを特徴とする臭気ガスの脱臭方法。   A method for deodorizing odor gas, characterized in that odor gas is biodeodorized in advance using a microorganism-immobilized carrier, and the biodeodorization treatment gas is further contacted with a metal phthalocyanine catalyst-containing solution for treatment. 使用した前記金属フタロシアニン触媒含有溶液に蓄積するイオウ等の固形物を固液分離により除去して、循環使用することを特徴とする請求項1記載の臭気ガスの脱臭方法。   2. The odor gas deodorizing method according to claim 1, wherein solid substances such as sulfur accumulated in the used metal phthalocyanine catalyst-containing solution are removed by solid-liquid separation and recycled. 臭気ガスを生物処理する微生物固定化担体を充填した生物脱臭塔を前段に設置し、後段に金属フタロシアニン触媒含有溶液を散布する気液接触反応塔を設置し、生物脱臭塔からの処理ガスを金属フタロシアニン触媒溶液を散布する気液接触反応塔に導入する配管を設けたことを特徴とする臭気ガスの脱臭装置。   A biological deodorization tower filled with a microorganism-immobilized carrier that biologically treats odorous gas is installed in the front stage, and a gas-liquid contact reaction tower that sprays a solution containing a metal phthalocyanine catalyst is installed in the rear stage, and the processing gas from the biological deodorization tower is metalized. An odor gas deodorizing apparatus comprising a pipe for introducing a phthalocyanine catalyst solution into a gas-liquid contact reaction tower. 前記気液接触反応塔で使用された金属フタロシアニン触媒含有溶液より固形物を取り除く固液分離装置を前記気液接触反応塔に備えることを特徴とする請求項3記載の臭気ガスの脱臭装置。
The odor gas deodorization apparatus according to claim 3, wherein the gas-liquid contact reaction tower is provided with a solid-liquid separation device for removing solids from the metal phthalocyanine catalyst-containing solution used in the gas-liquid contact reaction tower.
JP2004051692A 2004-02-26 2004-02-26 Deodorization method and apparatus for odor gas Pending JP2005238112A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101293939B1 (en) * 2012-12-26 2013-08-19 주식회사 지앤이테크 Deodorization unit generated from the sewage and waste water
CN105771605A (en) * 2016-05-10 2016-07-20 四川西油致诚石油技术有限公司 Efficient deodorization treatment device for biochemical wastewater and wastegas
CN111617612A (en) * 2019-02-28 2020-09-04 中国石油化工股份有限公司 Refinery enterprise parking maintenance waste gas treatment method and system

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101293939B1 (en) * 2012-12-26 2013-08-19 주식회사 지앤이테크 Deodorization unit generated from the sewage and waste water
CN105771605A (en) * 2016-05-10 2016-07-20 四川西油致诚石油技术有限公司 Efficient deodorization treatment device for biochemical wastewater and wastegas
CN111617612A (en) * 2019-02-28 2020-09-04 中国石油化工股份有限公司 Refinery enterprise parking maintenance waste gas treatment method and system

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