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JP6970631B2 - Operation method of volatile organic compound processing equipment - Google Patents
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JP6970631B2 - Operation method of volatile organic compound processing equipment - Google Patents

Operation method of volatile organic compound processing equipment Download PDF

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JP6970631B2
JP6970631B2 JP2018043169A JP2018043169A JP6970631B2 JP 6970631 B2 JP6970631 B2 JP 6970631B2 JP 2018043169 A JP2018043169 A JP 2018043169A JP 2018043169 A JP2018043169 A JP 2018043169A JP 6970631 B2 JP6970631 B2 JP 6970631B2
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彰夫 松岡
晃弘 塔本
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Kurimoto Ltd
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Description

この発明は、揮発性有機化合物を含むガスを排出する前に、ガスから揮発性有機化合物を処理する装置に関する。 The present invention relates to an apparatus for treating a volatile organic compound from the gas before discharging the gas containing the volatile organic compound.

工場から発生する排ガスには、そのまま大気中に排出すると問題を起こす揮発性有機化合物が含まれる場合がある。この場合、排ガスを大気中に排出する前に、含有している揮発性有機化合物を処理しなければならない。その方法として、活性炭等の吸着剤を内蔵した吸着塔で、排ガス中に含まれる揮発性有機化合物を吸着剤に吸着させ、ガス中の濃度を低減させて大気へ排出する。その後、吸着塔に水蒸気を導入して吸着剤から揮発性有機化合物を脱着させて吸着塔を再利用可能にするとともに、揮発性有機化合物を処理するという吸脱着方式が一般的である。 Exhaust gas generated from factories may contain volatile organic compounds that cause problems if they are discharged into the atmosphere as they are. In this case, the volatile organic compounds contained must be treated before the exhaust gas is discharged into the atmosphere. As a method for this, a volatile organic compound contained in the exhaust gas is adsorbed on the adsorbent by an adsorption tower having an adsorbent such as activated carbon, and the concentration in the gas is reduced and discharged to the atmosphere. After that, a suction / desorption method is generally used in which water vapor is introduced into the adsorption tower to desorb the volatile organic compound from the adsorbent so that the adsorption tower can be reused and the volatile organic compound is treated.

これは活性炭が揮発性有機化合物を吸着する吸着量が基本的には温度に依存することを利用している。活性炭が低温であるほど吸着量は多くなり、高温であるほど吸着量は少なくなる。従って、活性炭が低温の状態で吸着させ、脱着させる際には高温にする。活性炭を高温にして脱着させるには、高温の脱着用水蒸気や、燃料を燃焼させた高温ガス、高温ガスの熱量で水を蒸発させて脱着用水蒸気を生成させた後の残存ガスなど、熱量を有するガスを導入することが行われている(特許文献1)。 This utilizes the fact that the amount of adsorption of activated carbon that adsorbs volatile organic compounds basically depends on the temperature. The lower the temperature of the activated carbon, the higher the adsorption amount, and the higher the temperature, the lower the adsorption amount. Therefore, the activated carbon is adsorbed at a low temperature, and when it is desorbed, it is heated to a high temperature. To desorb activated carbon at a high temperature, the amount of heat such as high-temperature desorption steam, high-temperature gas that burns fuel, and residual gas after evaporating water with the amount of heat of the high-temperature gas to generate desorption steam is used. It is carried out to introduce the gas having (Patent Document 1).

この吸着塔を用いた揮発性有機化合物処理装置の運用にあたっては、脱着用水蒸気を生成するための燃料がコストの大半を占めているため、できるだけ熱効率を向上させることが望ましい。脱着させた揮発性有機化合物を燃焼させ、その燃焼熱を利用して脱着用水蒸気の生成を補助させ、燃料の消費量を抑制することが検討されている。 In the operation of the volatile organic compound processing apparatus using this adsorption tower, it is desirable to improve the thermal efficiency as much as possible because the fuel for generating the desorbed steam accounts for most of the cost. It has been studied to burn desorbed volatile organic compounds and utilize the heat of combustion to assist the generation of desorbed steam to suppress fuel consumption.

一方、吸着塔に導入する排ガスに含まれている揮発性有機化合物が多すぎると、装置負荷が高くなりすぎてしまう。高濃度の揮発性有機化合物を含有する場合は、排ガスは導入前に別の手法であらかじめ揮発性有機化合物の量を削減しておき、それでも残存する揮発性有機化合物について吸着塔を用いることが望ましい。特許文献2には、ガスの露点温度に応じて適切な温度にまで予め冷却する温度制御を行った上でガスを導入することが提案されている。 On the other hand, if the amount of volatile organic compounds contained in the exhaust gas introduced into the adsorption tower is too large, the load on the device becomes too high. When a high concentration of volatile organic compounds is contained, it is desirable to reduce the amount of volatile organic compounds in advance by another method for exhaust gas before introduction, and to use an adsorption tower for the remaining volatile organic compounds. .. Patent Document 2 proposes to introduce a gas after performing temperature control in advance to cool the gas to an appropriate temperature according to the dew point temperature of the gas.

特開2014−168741号公報Japanese Unexamined Patent Publication No. 2014-168741 特開2014−526号公報Japanese Unexamined Patent Publication No. 2014-526

この発明は、揮発性有機化合物処理装置の運用にあたって、作業効率を維持しながら蒸気の運用にかかるエネルギーや負荷をさらに低減させることを目的とする。 It is an object of the present invention to further reduce the energy and load required for the operation of steam while maintaining the work efficiency in the operation of the volatile organic compound processing apparatus.

この発明は、
揮発性有機化合物を吸着する活性炭を充填する吸着剤収容部を有する吸着塔により、揮発性有機化合物含有ガスの揮発性有機化合物濃度を前記活性炭に吸着させることで減少させ、
吸着後は高温のガスを接触させて前記活性炭から上記揮発性有機化合物を脱着させる揮発性有機化合物処理装置を運用するにあたり、
前記吸着塔内には内部の気体温度を測定可能な温度計が備えてあり、
前記高温のガスとして脱着用水蒸気を用い、
導入する揮発性有機化合物含有ガスの温度を測定し、
前記温度が低いほど、導入する脱着用水蒸気の量を抑制する
運用方法により、上記の課題を解決したのである。
This invention
The concentration of the volatile organic compound in the volatile organic compound-containing gas is reduced by adsorbing the volatile organic compound to the activated carbon by using an adsorption tower having an adsorbent accommodating portion filled with the active carbon that adsorbs the volatile organic compound.
In operating a volatile organic compound processing apparatus that desorbs the volatile organic compound from the activated carbon by contacting it with a high-temperature gas after adsorption.
The adsorption tower is equipped with a thermometer capable of measuring the internal gas temperature.
Detachable steam was used as the high temperature gas, and
Measure the temperature of the volatile organic compound-containing gas to be introduced,
The lower the temperature, the more the amount of desorbed water vapor introduced was suppressed, and the above-mentioned problem was solved by the operation method.

これは次のような新たな知見に基づくものである。一旦吸着を終えた活性炭の吸着性能を十分に復活させるためには、十分な脱着が必要であるため、加熱目標温度は一律に設定することが一般的であった。しかし、吸着を低温環境で行う場合にはその性質上十分な吸着量が見込めるため、吸着性能を復活させるために脱着を徹底させる必要はなく、必要とする加熱量を削減できることがわかった。その上で、水蒸気を用いる場合は空気などのガスを用いる場合とは昇温に必要なガスの量が特異的に異なることが確かめられた。 This is based on the following new findings. In order to fully restore the adsorption performance of the activated carbon once adsorbed, sufficient desorption is required, so it was common to set the heating target temperature uniformly. However, when adsorption is performed in a low temperature environment, a sufficient amount of adsorption can be expected due to its nature, so it is not necessary to thoroughly desorb in order to restore the adsorption performance, and it was found that the required heating amount can be reduced. On that basis, it was confirmed that the amount of gas required for temperature rise is specifically different when water vapor is used than when gas such as air is used.

従来は季節に拘わらず夏季の運用と同じ温度にまで活性炭を加熱して脱着させていたが、冬季は活性炭も導入される揮発性有機化合物含有ガスも低温になり、吸着できる量は夏季よりも向上する。すると、脱着を徹底しておかなくても活性炭を外気温によって十分冷却しておけば、必要とする吸着量を確保することができる。 In the past, activated carbon was heated and desorbed to the same temperature as in summer operation regardless of the season, but in winter the temperature of the volatile organic compound-containing gas into which activated carbon is introduced becomes lower, and the amount that can be adsorbed is higher than in summer. improves. Then, if the activated carbon is sufficiently cooled by the outside air temperature without thorough desorption, the required adsorption amount can be secured.

特に、吸着温度が30℃前後の場合と、35℃前後の場合とでは、わずかな温度差であるにも拘わらず、必要な脱着率を確保するために必要な水蒸気の量が大きく異なることを見出した。35℃前後の場合に必要とする水蒸気の量を基準として比べると、30℃前後の場合に必要な水蒸気の量は、2/3以下から半分近くにまで低減できることが見出された。さらに低温の環境では、30℃前後までの低減傾向よりも温度低下量に比べた水蒸気の低減幅は小さくはなるが、30℃前後までの急激な低減傾向にさらに加えて低減できるため、35℃前後の環境に比べての低減幅はさらに拡大する。従って、冬季に限らず春季や秋季のような、夏季との温度の違いがそれほど大きくない時期での吸着環境であっても、その吸着の際のわずかな違いによって生じる、必要な蒸気量の違いを、35℃前後と30℃前後との間の特異的違いを踏まえて決定することで、蒸気量を大幅に削減することができる。 In particular, the amount of water vapor required to secure the required desorption rate differs greatly between the case where the adsorption temperature is around 30 ° C and the case where the adsorption temperature is around 35 ° C, despite the slight temperature difference. I found it. Comparing the amount of water vapor required at around 35 ° C as a reference, it was found that the amount of water vapor required at around 30 ° C can be reduced from 2/3 or less to nearly half. In a lower temperature environment, the amount of water vapor reduction compared to the amount of temperature decrease is smaller than the decrease tendency to around 30 ° C, but it can be further reduced in addition to the rapid reduction tendency to around 30 ° C, so it is 35 ° C. The amount of reduction compared to the environment before and after is further expanded. Therefore, even in the adsorption environment not only in winter but also in the time when the temperature difference from summer is not so large, such as spring and autumn, the difference in the required amount of steam caused by the slight difference in adsorption occurs. The amount of steam can be significantly reduced by determining the temperature based on the specific difference between about 35 ° C. and about 30 ° C.

この発明により、脱着用水蒸気の生成に必要とする燃料等のエネルギーを削減でき、装置全体のエネルギー効率を向上させることができる。 INDUSTRIAL APPLICABILITY According to the present invention, it is possible to reduce the energy required for the generation of desorption steam and the like, and to improve the energy efficiency of the entire device.

この発明にかかる運用方法を実行する揮発性有機化合物処理装置の構成例図Configuration example diagram of a volatile organic compound processing apparatus for executing the operation method according to the present invention.

以下、この発明の実施形態を説明する。この発明は、揮発性有機化合物含有ガスの濃度を低減させて大気中へ排出可能とし、その分の揮発性有機化合物を吸着剤に吸着させる揮発性有機化合物の処理装置10の運用方法である。この処理装置10で吸着を行う吸着塔11は吸着剤として活性炭を有し、吸着された揮発性有機化合物は加熱した水蒸気と接触させることで吸着剤から脱着させて、吸着剤を繰り返し利用できる。脱着させた揮発性有機化合物は回収して加熱した水蒸気を得るための燃料として使用する。図1はこれらの一連のサイクルを行う処理装置10の全体像の例を示す。 Hereinafter, embodiments of the present invention will be described. The present invention is an operation method of a volatile organic compound processing apparatus 10 that reduces the concentration of a volatile organic compound-containing gas so that it can be discharged into the atmosphere, and adsorbs the volatile organic compound to the adsorbent. The adsorption tower 11 that adsorbs with this processing device 10 has activated carbon as an adsorbent, and the adsorbed volatile organic compounds can be desorbed from the adsorbent by contacting with heated steam, and the adsorbent can be used repeatedly. The desorbed volatile organic compounds are recovered and used as fuel for obtaining heated steam. FIG. 1 shows an example of an overall image of the processing apparatus 10 that performs these series of cycles.

この発明にかかる運用方法で運用する処理装置で処理する揮発性有機化合物とは、常圧で加熱することで気体になり得る有機化合物であり、特に常温で液体であるものが吸着処理しやすい。例えば、メタノール、エタノール、イソプロピルアルコール等の炭素数が1〜8程度のアルコール、トルエン、ベンゼンなどの芳香族有機化合物などの、炭化水素系の溶剤が挙げられる。 The volatile organic compound processed by the processing apparatus operated by the operation method according to the present invention is an organic compound that can become a gas by heating at normal pressure, and a compound that is liquid at room temperature is particularly easy to be adsorbed. Examples thereof include hydrocarbon solvents such as alcohols having about 1 to 8 carbon atoms such as methanol, ethanol and isopropyl alcohol, and aromatic organic compounds such as toluene and benzene.

個々の吸着塔11は角形又は円筒形であり、装置内部には、揮発性有機化合物を吸着し、加熱により脱着できる吸着剤を充填させた吸着剤収容部12を設けてある。この吸着剤としては、粒状活性炭を用いることができる。吸着塔11の内部を上下方向に通過するためには、必ず吸着剤収容部12を通過しなければならない。吸着剤収容部12の底面と上面はどちらも吸着塔11内に格納されている。 Each adsorption tower 11 has a rectangular shape or a cylindrical shape, and an adsorbent accommodating portion 12 filled with an adsorbent that adsorbs volatile organic compounds and can be desorbed by heating is provided inside the apparatus. Granular activated carbon can be used as this adsorbent. In order to pass through the inside of the adsorption tower 11 in the vertical direction, it must pass through the adsorbent accommodating portion 12. Both the bottom surface and the top surface of the adsorbent accommodating portion 12 are housed in the adsorbent tower 11.

吸着塔11の活性炭を収容する吸着剤収容部12には温度計13が設けられてあり、後述するコントロールバルブ24に接続されている。 A thermometer 13 is provided in the adsorbent accommodating portion 12 for accommodating the activated carbon of the adsorption tower 11, and is connected to a control valve 24 described later.

吸着塔11の吸着剤収容部12より上端側には、揮発性有機化合物含有ガスAの導入口17が設けてあり、原ガスブロワ14によって生じた圧力によって揮発性有機化合物含有ガスAが導入される。吸着剤収容部12より下端側には、揮発性有機化合物が吸着剤に吸着されることでその濃度が低下した処理後ガスBの排出口18が設けてある。排出口18は大気中へ放出するものである。 An introduction port 17 for the volatile organic compound-containing gas A is provided on the upper end side of the adsorbent accommodating portion 12 of the adsorption tower 11, and the volatile organic compound-containing gas A is introduced by the pressure generated by the raw gas blower 14. .. On the lower end side of the adsorbent accommodating portion 12, a discharge port 18 for the treated gas B whose concentration is reduced by adsorbing the volatile organic compound to the adsorbent is provided. The discharge port 18 discharges into the atmosphere.

また、吸着塔11の吸着剤収容部12の下端よりも下に、脱着用水蒸気Fの水蒸気供給口25が設けてある。また、揮発性有機化合物を脱着した水蒸気有機化合物同伴ガスKを抜き出すための水蒸気排出口26が、吸着剤収容部12の上端よりも上端側に設けてある。この水蒸気排出口26から水蒸気有機化合物同伴ガスKが搬送される。 Further, a steam supply port 25 for the desorbed steam F is provided below the lower end of the adsorbent accommodating portion 12 of the adsorption tower 11. Further, a steam discharge port 26 for extracting the steam organic compound-accompanied gas K from which the volatile organic compound has been desorbed is provided on the upper end side of the upper end of the adsorbent accommodating portion 12. The water vapor organic compound-accompanied gas K is conveyed from the water vapor discharge port 26.

水蒸気有機化合物同伴ガスKは、コンデンサ15に供給されて冷却水Pにより冷却される。冷却により水蒸気有機化合物同伴ガスKに含まれていた揮発性有機化合物を分離回収し(回収有機化合物Q)、残りのガスは排気Rとする。 The steam organic compound-accompanied gas K is supplied to the condenser 15 and cooled by the cooling water P. By cooling, the volatile organic compound contained in the gas K accompanied by the steam organic compound is separated and recovered (recovered organic compound Q), and the remaining gas is used as exhaust R.

それぞれの吸着塔11への入口及び出口にはバルブが設けてある。すなわち、導入口17にはバルブ21を、排出口18にはバルブ22を、水蒸気排出口26にはバルブ23をそれぞれ設けてある。また、水蒸気供給口25にはコントロールバルブ24が設けてある。 Valves are provided at the inlet and outlet to each suction tower 11. That is, a valve 21 is provided at the introduction port 17, a valve 22 is provided at the discharge port 18, and a valve 23 is provided at the steam discharge port 26. Further, the steam supply port 25 is provided with a control valve 24.

揮発性有機化合物含有ガスAを処理する吸着工程では、バルブ21とバルブ22を開放し、バルブ23とコントロールバルブ24とを閉鎖して、原ガスブロワ14にて導入口17から揮発性有機化合物含有ガスAを活性炭12に通気する。このとき、温度計13で吸着開始時の温度を測定しておく。この温度は基本的に活性炭12の温度であり、揮発性有機化合物含有ガスAの温度でもある。十分に吸着塔11が冷却されており、揮発性有機化合物含有ガスAの濃度が50〜1000ppm程度であれば、この温度は運用時にほぼ等しくなるため同視できる。 In the adsorption step for treating the volatile organic compound-containing gas A, the valve 21 and the valve 22 are opened, the valve 23 and the control valve 24 are closed, and the raw gas blower 14 is used to open the volatile organic compound-containing gas from the introduction port 17. A is aerated through the activated carbon 12. At this time, the temperature at the start of adsorption is measured with the thermometer 13. This temperature is basically the temperature of the activated carbon 12, and is also the temperature of the volatile organic compound-containing gas A. If the adsorption tower 11 is sufficiently cooled and the concentration of the volatile organic compound-containing gas A is about 50 to 1000 ppm, this temperature is almost the same during operation and can be regarded as the same.

活性炭12が揮発性有機化合物を吸着し、揮発性有機化合物を除去された処理後ガスBが排出口18から排出される。活性炭12が十分に揮発性有機化合物を吸着し、算出される吸着量が許容値を超えた時点で、吸着を停止し、脱着工程へと切り替える。 The activated carbon 12 adsorbs the volatile organic compound, and the treated gas B from which the volatile organic compound has been removed is discharged from the discharge port 18. When the activated carbon 12 sufficiently adsorbs the volatile organic compound and the calculated adsorption amount exceeds the permissible value, the adsorption is stopped and the process is switched to the desorption step.

脱着工程では、吸着工程とは逆にバルブ21,22を閉鎖し、バルブ23及びコントロールバルブ24を開放して、脱着用水蒸気Fを活性炭に接触させる。このとき、コントロールバルブ24の開放量、すなわち脱着用水蒸気Fの供給量を、先に測定した吸着開始時における温度計13の値に応じて調整する。具体的には、吸着工程での前記温度計13の値が低いほど、導入する脱着用水蒸気Fの量を抑制する。吸着時の温度が低いほど、吸着できる揮発性有機化合物の量が多くなるため、脱着工程後に再度吸着工程を行うにあたって、脱着を徹底していなくても、吸着工程に必要なだけの潜在的吸着量を確保できるようになるからである。すなわち、吸着開始時の温度が低い場合には、脱着用水蒸気Fの量を抑制でき、脱着用水蒸気Fを生成するために必要な燃料の消費を抑制でき、装置の運用負荷を低下させることができる。 In the desorption step, the valves 21 and 22 are closed, the valves 23 and the control valve 24 are opened, and the desorption steam F is brought into contact with the activated carbon, contrary to the adsorption step. At this time, the open amount of the control valve 24, that is, the supply amount of the attached / detached steam F is adjusted according to the value of the thermometer 13 at the start of adsorption measured earlier. Specifically, the lower the value of the thermometer 13 in the adsorption step, the more the amount of desorbed water vapor F to be introduced is suppressed. The lower the temperature at the time of adsorption, the larger the amount of volatile organic compounds that can be adsorbed. Therefore, when the adsorption step is performed again after the desorption step, even if the desorption is not thoroughly performed, the potential adsorption required for the adsorption step is sufficient. This is because the amount can be secured. That is, when the temperature at the start of adsorption is low, the amount of desorption steam F can be suppressed, the consumption of fuel required to generate the desorption steam F can be suppressed, and the operational load of the device can be reduced. can.

ただし、この調整値は一般的なガスの吸着等温線に従って決定するのではなく、吸着塔の性質毎に、温度毎の吸着量及び脱着量を測定した上で行うことが好ましい。脱着用水蒸気Fを用いた脱着の場合は、水蒸気ではないガスにおける吸着等温線の挙動には従わないことが確認されており、好適な運用のためには、処理するガスの除去率として80%以上、望ましくは90%となるように、それに見合う蒸気量を供給することが望ましい。 However, this adjustment value is not determined according to a general gas adsorption isotherm, but is preferably performed after measuring the adsorption amount and the desorption amount for each temperature for each property of the adsorption tower. Desorption It has been confirmed that desorption using steam F does not follow the behavior of the adsorption isotherm in a gas that is not steam, and for proper operation, the removal rate of the gas to be treated is 80%. As mentioned above, it is desirable to supply a steam amount commensurate with the amount so as to be preferably 90%.

そのように十分な除去率を実現するだけの脱着に必要な蒸気量は、吸着温度が35℃前後の場合を基準とすると、吸着温度が30℃前後の場合には急激に減少する。35℃前後と30℃前後との間に必要蒸気量が特異的に変化する特異点があると考えられる。そこで、吸着温度の条件として、34℃以上と31℃以下とを区別する。34℃以上は前記の35℃前後の状況に対応し、夏季における運用に対応する。この夏季基準となる吸着温度としては34℃以上37℃以下が好ましい。 The amount of vapor required for desorption to achieve such a sufficient removal rate sharply decreases when the adsorption temperature is around 30 ° C., based on the case where the adsorption temperature is around 35 ° C. It is considered that there is a singular point where the required vapor amount changes specifically between around 35 ° C and around 30 ° C. Therefore, as a condition of the adsorption temperature, it is distinguished between 34 ° C. or higher and 31 ° C. or lower. The temperature of 34 ° C or higher corresponds to the above-mentioned situation of around 35 ° C, and corresponds to the operation in the summer. The adsorption temperature as a reference for this summer is preferably 34 ° C. or higher and 37 ° C. or lower.

吸着温度が31℃以下である場合、前記夏季基準の際に十分な除去率を実現するために供給する蒸気量Vsummerに対して、2/3以下の蒸気量Vexで十分な除去率を実現できる。15℃以上31℃以下の吸着温度では、Vsummerに対して1/3以上2/3以下となる蒸気量で運用することが望ましい。0℃以上15℃以下の吸着温度では、Vsummerに対して1/4以上1/2以下となる蒸気量で運用することが望ましい。 When the adsorption temperature is 31 ° C. or less, a sufficient removal rate can be realized with a steam amount Vex of 2/3 or less with respect to the steam amount Vsummer supplied to realize a sufficient removal rate at the time of the summer standard. .. At the adsorption temperature of 15 ° C. or higher and 31 ° C. or lower, it is desirable to operate with a steam amount of 1/3 or more and 2/3 or less of Vsummer. At the adsorption temperature of 0 ° C. or higher and 15 ° C. or lower, it is desirable to operate with a steam amount of 1/4 or more and 1/2 or less of Vsummer.

脱着された揮発性有機化合物は、温度が低下した脱着用水蒸気とともに水蒸気有機化合物同伴ガスKとなって水蒸気排出口26から排出される。この水蒸気有機化合物同伴ガスKをコンデンサ15に導入し、冷却水Pで冷却して含有した揮発性有機化合物を回収し(回収有機化合物Q)、残りのガスを排気(R)して処理する。 The desorbed volatile organic compound becomes a water vapor organic compound-accompanied gas K together with the desorbed water vapor whose temperature has dropped, and is discharged from the water vapor discharge port 26. This steam organic compound-accompanied gas K is introduced into the condenser 15, cooled with cooling water P to recover the contained volatile organic compound (recovered organic compound Q), and the remaining gas is exhausted (R) for treatment.

以下、この発明の実施例を示す。(株)栗本鐵工所製吸着塔(活性炭層面積:1.0m、活性炭層厚:0.3m)に、通過風速0.5m/sとなるように、トルエン濃度300ppmとなる揮発性有機化合物含有ガスAを導入し、吸着時間80分となるように吸着を行った。脱着時間は40分とし、運用上脱着が完了したとみなす必要な除去率の設定を90%とした。 Hereinafter, examples of the present invention will be shown. Volatile organic compounds with a toluene concentration of 300 ppm so that the passing air velocity is 0.5 m / s in the adsorption tower (activated carbon layer area: 1.0 m 2, activated carbon layer thickness: 0.3 m) manufactured by Kurimoto, Ltd. The compound-containing gas A was introduced and adsorbed so that the adsorption time was 80 minutes. The desorption time was 40 minutes, and the removal rate required to be considered as complete desorption in operation was set to 90%.

吸着温度35℃で運用したとき、除去率90%に必要な蒸気量Vsummerは27kgとなった。このVsummerを基準とする。 When operated at an adsorption temperature of 35 ° C., the amount of steam required for a removal rate of 90%, Vsummer, was 27 kg. This Vsummer is used as a reference.

吸着温度30℃で運用したとき、除去率90%に必要な蒸気量Vex30は14kgとなり、Vsummerに対して52%にまで減少させることができた。 When operated at an adsorption temperature of 30 ° C., the amount of steam required for a removal rate of 90%, Vex30, was 14 kg, which could be reduced to 52% with respect to Vsummer.

吸着温度10℃で運用したとき、除去率90%に必要な蒸気量Vex10は10kgとなり、Vsummerに対して37%にまで減少させることができた。 When operated at an adsorption temperature of 10 ° C., the amount of steam required for a removal rate of 90%, Vex10, was 10 kg, which could be reduced to 37% with respect to Vsummer.

10 処理装置
11 吸着塔
12 活性炭(吸着剤収容部)
13 温度計
14 原ガスブロワ
15 コンデンサ
17 導入口
18 排出口
21,22,23 バルブ
24 コントロールバルブ
25 水蒸気供給口
26 水蒸気排出口
A 揮発性有機化合物含有ガス
B 処理後ガス
F 脱着用水蒸気
K 水蒸気有機化合物同伴ガス
P 冷却水
Q 回収有機化合物
R 排気
10 Processing device 11 Adsorption tower 12 Activated carbon (adsorbent accommodating part)
13 Thermometer 14 Raw gas blower 15 Condenser 17 Inlet 18 Discharge port 21, 22, 23 Valve 24 Control valve 25 Steam supply port 26 Steam discharge port A Volatile organic compound-containing gas B After treatment Gas F Detachable water vapor K Steam organic compound Accompanying gas P Cooling water Q Recovered organic compound R Exhaust

Claims (2)

揮発性有機化合物を吸着する活性炭を充填する吸着剤収容部を有する吸着塔により、揮発性有機化合物含有ガスの揮発性有機化合物濃度を前記活性炭に吸着させることで減少させ、
吸着後は高温のガスを接触させて前記活性炭から上記揮発性有機化合物を脱着させる揮発性有機化合物処理装置を運用するにあたり、
前記吸着塔内には内部の気体温度を測定可能な温度計が備えてあり、
前記高温のガスとして脱着用水蒸気を用い、
導入する揮発性有機化合物含有ガスの温度を測定し、
前記温度が低いほど、導入する脱着用水蒸気の量を抑制する
揮発性有機化合物処理装置の運用方法。
The concentration of the volatile organic compound in the volatile organic compound-containing gas is reduced by adsorbing the volatile organic compound to the activated carbon by using an adsorption tower having an adsorbent accommodating portion filled with the active carbon that adsorbs the volatile organic compound.
In operating a volatile organic compound processing apparatus that desorbs the volatile organic compound from the activated carbon by contacting it with a high-temperature gas after adsorption.
The adsorption tower is equipped with a thermometer capable of measuring the internal gas temperature.
Detachable steam was used as the high temperature gas, and
Measure the temperature of the volatile organic compound-containing gas to be introduced,
An operation method of a volatile organic compound processing apparatus that suppresses the amount of desorbed water vapor to be introduced as the temperature is lower.
前記脱着用水蒸気の量の抑制幅を、
前記温度が34℃以上の際に導入すべき前記脱着用水蒸気の量を基準値とし、
前記温度が31℃以下の際に導入する前記脱着用水蒸気の量を、前記基準値の2/3以下に抑制する
請求項1に記載の揮発性有機化合物処理装置の運用方法。
The range of suppression of the amount of desorbed water vapor is
The amount of the desorbed water vapor to be introduced when the temperature is 34 ° C. or higher is used as a reference value.
The method for operating a volatile organic compound processing apparatus according to claim 1, wherein the amount of the desorbed water vapor introduced when the temperature is 31 ° C. or lower is suppressed to 2/3 or less of the reference value.
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