JP2013086024A - Organic solvent desorption method and organic solvent desorbing device - Google Patents

Organic solvent desorption method and organic solvent desorbing device Download PDF

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JP2013086024A
JP2013086024A JP2011228859A JP2011228859A JP2013086024A JP 2013086024 A JP2013086024 A JP 2013086024A JP 2011228859 A JP2011228859 A JP 2011228859A JP 2011228859 A JP2011228859 A JP 2011228859A JP 2013086024 A JP2013086024 A JP 2013086024A
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desorption
organic solvent
superheated steam
dry gas
tank
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JP5861177B2 (en
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Zenichi Takano
善一 高野
Toshihiko Sato
俊彦 佐藤
Masahiro Tanaka
将博 田中
Hirokazu Sugimori
博和 杉森
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Tokyo Metropolitan Industrial Technology Research Instititute (TIRI)
Morikawa Co Ltd
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Morikawa Co Ltd
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Abstract

PROBLEM TO BE SOLVED: To facilitate work for removing an organic solvent mixed in concentrated water by securing a high desorption rate and reducing the quantity of concentrated water generated after desorption when desorbing the organic solvent from an adsorbent having adsorbed organic solvent.SOLUTION: An organic solvent desorbing device includes; a desorption tank 1 filled with adsorbents having adsorbed organic solvents; a blower 2 and a heater 3 for supplying heated dry gas to the desorption tank 1; and a superheated steam generator 6 which supplies superheated steam to the desorption tank 1. An organic solvent desorption method carries out a first desorbing step in which the organic solvents are desorbed by supplying the dry gas to the adsorbents, and thereafter, a second desorbing step in which the organic solvents are further desorbed by supplying superheated steam to the adsorbents.

Description

本発明は、活性炭やゼオライト等の吸着剤に吸着された有機溶剤を脱着して回収するための有機溶剤の脱着方法および有機溶剤の脱着装置の技術分野に関するものである。   The present invention relates to a technical field of an organic solvent desorption method and an organic solvent desorption apparatus for desorbing and recovering an organic solvent adsorbed on an adsorbent such as activated carbon or zeolite.

一般に、トルエン、酢酸エチル、メチルエチルケトン、ジクロロメタン、クロロベンゼン、ノルマルプロピルアルコール、イソプロピルアルコール等の揮発性の高い有機溶剤は、化学工場、塗装工場、印刷工場、薬品工場、半導体製造工場、精密機械製造工場等の各種施設において、反応、抽出、コーティング、脱脂洗浄等の各種工程で溶剤として広く用いられている。この様な揮発性の高い有機溶剤がガス化して大気中に排出されると、光化学オキシダントや浮遊粒子状物質の要因になり、そこで、ガス化した有機溶剤を回収(除去)するための回収システムが必要とされる。
前記回収システムとしては、従来から、ガス化した有機溶剤を活性炭やゼオライト等の吸着剤に吸着させる一方、該有機溶剤が吸着された吸着剤から有機溶剤を脱着することで、吸着剤を繰り返して利用できるようにしたものが知られている。さらにこの様な回収システムにおいて、吸着剤から有機溶剤を脱着するにあたり、加熱した空気や窒素ガス等のドライガスをキャリアガスとして吸着剤に供給して脱着する方法が知られているが、この様なドライガスを用いた脱着は、脱着率、つまり、吸着剤からの有機溶剤の除去率があまり高くないという問題を有している。このため、ドライガスを用いた脱着では、未脱着有機溶剤が吸着剤に残存してしまうことになって、脱着後の吸着剤を用いて再度吸着しようとしたときに、吸着量が低下するという問題がある。
そこで従来、吸着剤から有機溶剤を脱着するにあたり、ドライガスに換えて過熱水蒸気をキャリアガスとして脱着槽に供給して脱着する方法が知られている(例えば、特許文献1参照)。この過熱水蒸気を用いた脱着は、過熱水蒸気の温度や圧力、流量等を適切に設定することで高い脱着率が得られことが確認されている。
In general, organic solvents with high volatility such as toluene, ethyl acetate, methyl ethyl ketone, dichloromethane, chlorobenzene, normal propyl alcohol, isopropyl alcohol, chemical factories, painting factories, printing factories, chemical factories, semiconductor manufacturing factories, precision machinery manufacturing factories, etc. Are widely used as solvents in various processes such as reaction, extraction, coating, and degreasing. When such a highly volatile organic solvent is gasified and discharged into the atmosphere, it becomes a factor of photochemical oxidants and suspended particulate matter, and there is a recovery system for recovering (removing) the gasified organic solvent. Is needed.
Conventionally, as the recovery system, the gasified organic solvent is adsorbed on an adsorbent such as activated carbon or zeolite, and the adsorbent is repeated by desorbing the organic solvent from the adsorbent on which the organic solvent is adsorbed. What is made available is known. Furthermore, in such a recovery system, when desorbing the organic solvent from the adsorbent, a method is known in which dry gas such as heated air or nitrogen gas is supplied to the adsorbent as a carrier gas and desorbed. Desorption using a dry gas has a problem that the desorption rate, that is, the removal rate of the organic solvent from the adsorbent is not so high. For this reason, in the desorption using dry gas, the non-desorbed organic solvent remains in the adsorbent, and the adsorption amount decreases when trying to adsorb again using the adsorbent after desorption. There's a problem.
Therefore, conventionally, a method for desorbing an organic solvent from an adsorbent by supplying superheated steam as a carrier gas to a desorption tank instead of dry gas is known (for example, see Patent Document 1). It has been confirmed that desorption using superheated steam can achieve a high desorption rate by appropriately setting the temperature, pressure, flow rate, etc. of superheated steam.

特開2011−125800号公報JP 2011-125800 A

しかしながら、前記過熱水蒸気を用いた脱着では、脱着された有機溶剤ガスと、キャリアとして用いた多量の水蒸気とが混合ガスとなって脱着槽から排出される。そして、この有機溶剤ガスと水蒸気との混合ガスを凝縮し、比重分離等により有機溶剤と凝縮水とに分離して回収した場合に、該回収した凝縮水中には多少なりとも有機溶剤が混入しており、このため、回収した凝縮水からさらに混入している有機溶剤を分離して除去するための除去処理を行なわないと、回収した凝縮水をそのまま外部に排出できないことになる。この凝縮水から有機溶剤を除去するための除去処理は、凝縮水量が多いほど、つまり、脱着に用いた過熱水蒸気の量が多いほど大規模な除去処理が必要であって困難であるという問題があり、ここに本発明の解決すべき課題がある。   However, in desorption using superheated steam, the desorbed organic solvent gas and a large amount of water vapor used as a carrier are mixed gas and discharged from the desorption tank. Then, when the mixed gas of the organic solvent gas and water vapor is condensed and separated into the organic solvent and condensed water by specific gravity separation or the like, the organic solvent is mixed in the collected condensed water. For this reason, the recovered condensed water cannot be discharged to the outside without performing a removal process for separating and removing the organic solvent further mixed from the recovered condensed water. The removal treatment for removing the organic solvent from the condensed water has a problem that the larger the amount of condensed water, that is, the larger the amount of superheated steam used for desorption, the larger the removal treatment becomes and the more difficult it is. There is a problem to be solved by the present invention.

本発明は、上記の如き実情に鑑みこれらの課題を解決することを目的として創作されたものであって、請求項1の発明は、有機溶剤を吸着した吸着剤から前記有機溶剤を脱着するための脱着方法であって、該脱着方法は、前記吸着剤にドライガスを供給して脱着する第一脱着工程と、該第一脱着工程で脱着された吸着剤に過熱水蒸気を供給して更に脱着する第二脱着工程とを備えることを特徴とする有機溶剤の脱着方法である。
請求項2の発明は、有機溶剤を吸着した吸着剤から前記有機溶剤を脱着するための脱着装置であって、該脱着装置は、前記有機溶剤を吸着した吸着剤が充填される脱着槽と、該脱着槽にドライガスを供給するドライガス供給手段と、脱着槽に過熱水蒸気を供給する過熱水蒸気供給手段と、前記ドライガスを供給して脱着する第一脱着工程の後に過熱水蒸気を供給して脱着する第二脱着工程を行なうべく脱着槽へのドライガス、過熱水蒸気の供給を切換える切換え手段とを備えて構成されることを特徴とする有機溶剤の脱着装置である。
請求項3の発明は、請求項2において、ドライガス供給手段は、脱着槽に供給されるドライガスを加熱する加熱器を含むと共に、該加熱器は、過熱水蒸気供給手段が発生する過熱水蒸気を熱媒としてドライガスを加熱する構成であることを特徴とする有機溶剤の脱着装置である。
The present invention has been made in view of the above-mentioned circumstances and has been created for the purpose of solving these problems. The invention of claim 1 is for desorbing the organic solvent from the adsorbent adsorbing the organic solvent. The desorption method includes a first desorption step in which a dry gas is supplied to the adsorbent for desorption, and superheated steam is supplied to the adsorbent desorbed in the first desorption step for further desorption. And a second desorption step. The method of desorbing an organic solvent.
The invention of claim 2 is a desorption device for desorbing the organic solvent from the adsorbent adsorbing the organic solvent, the desorption device comprising a desorption tank filled with the adsorbent adsorbing the organic solvent; Dry gas supply means for supplying dry gas to the desorption tank, superheated steam supply means for supplying superheated steam to the desorption tank, and superheated steam after the first desorption step of supplying and desorbing the dry gas. An organic solvent desorption apparatus comprising a switching means for switching the supply of dry gas and superheated steam to a desorption tank so as to perform a second desorption step of desorption.
According to a third aspect of the present invention, in the second aspect, the dry gas supply means includes a heater for heating the dry gas supplied to the desorption tank, and the heater uses the superheated steam generated by the superheated steam supply means. An organic solvent desorption apparatus having a configuration in which dry gas is heated as a heat medium.

請求項1または2の発明とすることにより、ドライガスを用いた第一脱着工程では脱着されずに吸着剤に残存している有機溶剤を、過熱水蒸気を用いた第二脱着工程によって確実に脱着できることになって、高い脱着率を確保できる。しかも、過熱水蒸気を用いた第二脱着工程は、ドライガスを用いて脱着された後の活性炭に対して行なわれるため、過熱水蒸気の使用量を大幅に低減することができる。この結果、脱着後の有機溶剤ガスと水蒸気との混合ガスを凝縮したときに生じる凝縮水が大幅に少なくなり、該凝縮水に混入する有機溶剤を除去するための除去処理を小規模にできることになって、除去処理の容易化、コスト低減に大きく貢献できる。
請求項3の発明とすることにより、第二脱着工程に用いられる過熱水蒸気を有効利用して第一脱着工程に用いられるドライガスを加熱できることになって、ドライガス加熱用の熱源を別途必要とせず、装置の兼用化、省エネルギー化が図れる。
According to the invention of claim 1 or 2, the organic solvent remaining in the adsorbent without being desorbed in the first desorption process using dry gas is surely desorbed in the second desorption process using superheated steam. As a result, a high desorption rate can be secured. And since the 2nd desorption process using superheated steam is performed with respect to the activated carbon after desorption using dry gas, the usage-amount of superheated steam can be reduced significantly. As a result, the condensed water generated when the mixed gas of the organic solvent gas and water vapor after desorption is condensed is greatly reduced, and the removal process for removing the organic solvent mixed in the condensed water can be made small scale. Thus, the removal process can be facilitated and the cost can be greatly reduced.
According to the invention of claim 3, the dry gas used in the first desorption step can be heated by effectively using the superheated steam used in the second desorption step, and a separate heat source for heating the dry gas is required. Therefore, the device can be shared and energy can be saved.

脱着装置のフローを示す図である。It is a figure which shows the flow of a desorption apparatus. 予備実験例の実験結果を示す表図である。It is a table | surface figure which shows the experimental result of a preliminary experiment example. 実施例の実験結果を示す表図である。It is a table | surface figure which shows the experimental result of an Example. 比較例の実験結果を示す表図である。It is a table | surface figure which shows the experimental result of a comparative example.

以下、本発明の実施の形態について、図面に基づいて説明する。図1は、脱着装置のフローを示す図であるが、該図1において、1は脱着槽であって、該脱着槽1には、有機溶剤が吸着された活性炭(本発明の吸着剤に相当する)が充填されている。   Hereinafter, embodiments of the present invention will be described with reference to the drawings. FIG. 1 shows a flow of a desorption apparatus. In FIG. 1, 1 is a desorption tank, and the desorption tank 1 has activated carbon adsorbed with an organic solvent (corresponding to the adsorbent of the present invention). Is filled).

また、2は前記脱着槽1の上流側に設けられるブロアであって、該ブロア2から圧送されたドライガス(本実施の形態では空気)は、加熱器3によって加熱されてから前記脱着槽1に供給される。この場合に、加熱器3から脱着槽1に至る配管4には第一開閉弁5が配されており、該第一開閉弁5によって、脱着槽1へのドライガスの供給の開閉を行なえるようになっている。尚、脱着槽1に供給されるドライガスの温度及び流量は、活性炭に吸着された有機溶剤の特性や吸着量等に応じて適宜設定される。また、前記ブロア2及び加熱器3は、本発明のドライガス供給手段を構成する。さらに、本発明のドライガスとは、空気、或いは水分を除去した空気、或いは窒素等の不活性ガス、或いは空気と不活性ガスとの混合ガス等の低水分状態のガスをいう。   Reference numeral 2 denotes a blower provided on the upstream side of the desorption tank 1, and the dry gas (air in the present embodiment) fed from the blower 2 is heated by the heater 3 and then the desorption tank 1. To be supplied. In this case, a first open / close valve 5 is arranged in the pipe 4 extending from the heater 3 to the desorption tank 1, and the first open / close valve 5 can open and close the supply of dry gas to the desorption tank 1. It is like that. The temperature and flow rate of the dry gas supplied to the desorption tank 1 are appropriately set according to the characteristics of the organic solvent adsorbed on the activated carbon, the adsorption amount, and the like. The blower 2 and the heater 3 constitute dry gas supply means of the present invention. Furthermore, the dry gas of the present invention refers to a low moisture state gas such as air, air from which moisture has been removed, inert gas such as nitrogen, or a mixed gas of air and inert gas.

さらに、6は前記ブロア2と並列する状態で脱着槽1の上流側に設けられる過熱水蒸気発生装置(本発明の過熱水蒸気供給手段に相当する)であって、該過熱水蒸気発生装置6は、100℃を越える過熱水蒸気(例えば、200℃〜350℃の水蒸気)を発生して前記脱着槽1に供給する。この場合に、過熱水蒸気発生装置6から脱着槽1に至る配管7には開度量調整可能な第二開閉弁8が配設されており、該第二開閉弁8によって、過熱水蒸気発生装置6から脱着槽1への過熱水蒸気の供給の開閉、及び供給される過熱水蒸気の圧力の調整を行なえるようになっている。尚、脱着槽1に供給される過熱水蒸気の温度及び流量は、活性炭に吸着された有機溶剤の特性や吸着量等に応じて適宜設定される。   Furthermore, 6 is a superheated steam generator (corresponding to the superheated steam supply means of the present invention) provided upstream of the desorption tank 1 in parallel with the blower 2, and the superheated steam generator 6 is 100 Superheated steam exceeding 200C (for example, steam at 200C to 350C) is generated and supplied to the desorption tank 1. In this case, a second opening / closing valve 8 capable of adjusting the opening degree is provided in the pipe 7 extending from the superheated steam generator 6 to the desorption tank 1, and the second opening / closing valve 8 allows the superheated steam generator 6 to The superheated steam supply to the desorption tank 1 can be opened and closed, and the pressure of the supplied superheated steam can be adjusted. The temperature and flow rate of the superheated steam supplied to the desorption tank 1 are appropriately set according to the characteristics of the organic solvent adsorbed on the activated carbon, the adsorption amount, and the like.

ここで、前記加熱器3は、過熱水蒸気発生装置6で発生した過熱水蒸気を熱媒として、ブロア2から圧送されたドライガスを加熱する構成になっている。この場合に、過熱水蒸気発生装置6から加熱器3に至る配管9には開度量調整可能な第三開閉弁10が配設されており、該第三開閉弁10によって、過熱水蒸気発生装置6から加熱器3への過熱水蒸気の供給の開閉、及び供給される加熱水蒸気の圧力の調整を行なえるようになっている。   Here, the heater 3 is configured to heat the dry gas fed from the blower 2 using the superheated steam generated by the superheated steam generator 6 as a heat medium. In this case, a third opening / closing valve 10 capable of adjusting the opening degree is provided in the pipe 9 extending from the superheated steam generator 6 to the heater 3, and the third open / close valve 10 allows the superheated steam generator 6 to The supply of superheated steam to the heater 3 can be opened and closed, and the pressure of the supplied heated steam can be adjusted.

そして、前記脱着槽1に充填された活性炭を脱着するにあたり、まず、第一脱着工程として、ブロア2から圧送されて加熱器3により加熱されたドライガスをキャリアガスとして脱着槽1に供給して、活性炭に吸着された有機溶剤を脱着する。このドライガスを用いた第一脱着工程は、脱着槽1の出口側に接続された濃度センサ11(例えば、ガスクロマトグラフィー)により測定される有機溶剤濃度が、予め設定される設定濃度以下まで低下した時点で終了させる。或いは、予め設定される設定時間経過後に終了させる。該第一脱着工程を終了させる設定時間、或いは設定濃度は、活性炭に吸着された有機溶剤の特性や吸着量等に応じて設定されるが、本実施の形態では、脱着前の吸着量に対して第一脱着工程で70%〜90%程度の脱着が行なわれるように、設定時間或いは設定濃度が設定されている。   Then, when desorbing the activated carbon filled in the desorption tank 1, first, as a first desorption process, dry gas fed from the blower 2 and heated by the heater 3 is supplied to the desorption tank 1 as a carrier gas. Desorb organic solvent adsorbed on activated carbon. In the first desorption step using the dry gas, the concentration of the organic solvent measured by the concentration sensor 11 (for example, gas chromatography) connected to the outlet side of the desorption tank 1 is lowered to a preset concentration or less. It ends when it does. Alternatively, the process is terminated after a preset time has elapsed. The set time or set concentration for ending the first desorption step is set according to the characteristics of the organic solvent adsorbed on the activated carbon, the adsorption amount, etc., but in this embodiment, the adsorption amount before desorption is Thus, the set time or set concentration is set so that about 70% to 90% of desorption is performed in the first desorption step.

続いて、第二脱着工程として、過熱水蒸気発生装置6で発生された過熱水蒸気を脱着槽1に供給して、前記第一脱着工程でドライガスにより脱着された活性炭から更に有機溶剤を脱着する。この過熱水蒸気を用いた第二脱着工程は、脱着槽1の出口側に接続された温度センサ12により測定されるガス温度が、予め設定される設定温度を越えた時点で終了させる。該第二脱着工程を終了させる設定温度は、活性炭に吸着された有機溶剤の沸点に応じて、該沸点よりも高い温度(例えば、有機溶剤の沸点よりも10℃高い温度)が設定される。これは、脱着中においては、脱着槽1の出口側温度が有機溶剤の沸点近傍に保持される(脱着中は、有機溶剤の気化熱により過熱水蒸気の温度が低下してバランスするためと推論される)一方、脱着終了後は、脱着槽1の出口側温度が過熱水蒸気の供給温度近くまで急激に上昇することが実験により確認されているためである。   Subsequently, as the second desorption process, the superheated steam generated by the superheated steam generator 6 is supplied to the desorption tank 1, and the organic solvent is further desorbed from the activated carbon desorbed by the dry gas in the first desorption process. The second desorption process using superheated steam is terminated when the gas temperature measured by the temperature sensor 12 connected to the outlet side of the desorption tank 1 exceeds a preset temperature. The set temperature for ending the second desorption step is set to a temperature higher than the boiling point (for example, a temperature 10 ° C. higher than the boiling point of the organic solvent) according to the boiling point of the organic solvent adsorbed on the activated carbon. This is inferred that during the desorption, the outlet side temperature of the desorption tank 1 is maintained near the boiling point of the organic solvent (during desorption, the temperature of the superheated steam is lowered and balanced by the heat of vaporization of the organic solvent). On the other hand, after completion of the desorption, it has been confirmed by experiments that the temperature on the outlet side of the desorption tank 1 rapidly rises to near the supply temperature of the superheated steam.

而して、活性炭から有機溶剤を脱着する脱着工程として、まず、ドライガスを用いた第一脱着工程が行なわれ、続けて、過熱水蒸気を用いた第二脱着工程が行なわれる。そして、ドライガスを用いた第一脱着工程によって、活性炭から大部分(例えば、吸着量の70%〜90%)の有機溶剤が脱着され、続けて行なわれる過熱水蒸気を用いた第二脱着工程によって、第一脱着工程で脱着されずに活性炭に残存している有機溶剤の殆ど(例えば、第一脱着工程での脱着分も含めて吸着量の99%〜略100%)が確実に脱着されるようになっている。尚、第一脱着工程中は、加熱器3から脱着槽1に至る配管4に配設の第一開閉弁5が開き、過熱水蒸気発生装置6から脱着槽1に至る配管7に配設の第二開閉弁8が閉じるように制御され、また、第二脱着工程中は、第一開閉弁5が閉じ第二開閉弁8が開くように制御され、これにより、第一脱着工程ではドライガスが脱着槽1に供給され、また、第二脱着工程では過熱水蒸気が脱着槽1に供給されることになるが、これら第一開閉弁5および第二開閉弁8は、本発明の脱着槽へのドライガス、過熱水蒸気の供給を切換える切換え手段に相当する。また、前記脱着槽1、ブロア2及び加熱器3(ドライガス供給手段)、過熱水蒸気発生装置6(過熱水蒸気供給手段)、第一開閉弁5及び第二開閉弁8(切換え手段)は、本発明の脱着装置を構成する。   Thus, as a desorption process for desorbing the organic solvent from the activated carbon, first, a first desorption process using dry gas is performed, and then a second desorption process using superheated steam is performed. And by the 1st desorption process using dry gas, most organic solvents (for example, 70%-90% of adsorption amount) are desorbed from activated carbon, and the 2nd desorption process using superheated steam performed continuously is performed. In addition, most of the organic solvent remaining on the activated carbon without being desorbed in the first desorption step (for example, 99% to about 100% of the adsorption amount including the desorption amount in the first desorption step) is surely desorbed. It is like that. During the first desorption process, the first on-off valve 5 provided in the pipe 4 extending from the heater 3 to the desorption tank 1 is opened, and the first open / close valve 5 provided in the pipe 7 extending from the superheated steam generator 6 to the desorption tank 1 is opened. The two on-off valves 8 are controlled to be closed, and during the second desorption process, the first on-off valve 5 is controlled to be closed and the second on-off valve 8 is opened. The superheated steam is supplied to the desorption tank 1 in the second desorption process, and the first on-off valve 5 and the second on-off valve 8 are connected to the desorption tank of the present invention. This corresponds to switching means for switching the supply of dry gas and superheated steam. The desorption tank 1, blower 2 and heater 3 (dry gas supply means), superheated steam generator 6 (superheated steam supply means), first on-off valve 5 and second on-off valve 8 (switching means) The desorption apparatus of the invention is configured.

一方、13は前記脱着槽1の下流側に設けられる予冷凝縮器であって、該予冷凝縮器13は、工業用水を冷媒として、脱着槽1から排出された混合ガスを冷却する。該脱着槽1から排出される混合ガスは、第一脱着工程においては活性炭から脱着された有機溶剤ガスとドライガスとの混合ガスであり、また、第二脱着工程においては活性炭から脱着された有機溶剤ガスと水蒸気との混合ガスであるが、これら混合ガスが予冷凝縮器13によって冷却されることによって、有機溶剤ガスおよび水蒸気の一部が液化する。そして、該液化された有機溶剤および凝縮水は凝縮液タンク14にトラップされた後、比重分離器、蒸留分離器等の分離器15により有機溶剤と凝縮水とに分離されて、それぞれ有機溶剤回収タンク16、凝縮水回収タンク17に回収される。   On the other hand, 13 is a precooling condenser provided on the downstream side of the desorption tank 1, and the precooling condenser 13 cools the mixed gas discharged from the desorption tank 1 using industrial water as a refrigerant. The mixed gas discharged from the desorption tank 1 is a mixed gas of an organic solvent gas and dry gas desorbed from activated carbon in the first desorption step, and an organic desorbed from activated carbon in the second desorption step. Although it is a mixed gas of solvent gas and water vapor, when these mixed gases are cooled by the precooling condenser 13, the organic solvent gas and a part of the water vapor are liquefied. The liquefied organic solvent and condensed water are trapped in the condensate tank 14 and then separated into an organic solvent and condensed water by a separator 15 such as a specific gravity separator and a distillation separator, respectively. It is recovered in the tank 16 and the condensed water recovery tank 17.

さらに、18は前記凝縮液タンク14の下流側に設けられる低温凝縮器であって、該低温凝縮器18は、前記予冷凝縮器13によって液化されなかった混合ガスを、冷却器19によって冷却された低温(例えば、−5℃〜5℃)の冷媒を用いて冷却して液化する。そして、該低温凝縮器18によって液化された凝縮液は、有機溶剤と凝縮水と分離されて、それぞれ有機溶剤回収タンク20、凝縮水回収タンク21に回収される。尚、凝縮器としては、前記低温凝縮器18に代えて、加圧深冷型の凝縮器等を用いることもできる。   Further, 18 is a low-temperature condenser provided on the downstream side of the condensate tank 14, and the low-temperature condenser 18 has cooled the mixed gas that has not been liquefied by the pre-cooling condenser 13 by a cooler 19. It cools and liquefies using a low temperature (for example, -5 degreeC-5 degreeC) refrigerant | coolant. The condensate liquefied by the low-temperature condenser 18 is separated from the organic solvent and condensed water, and is recovered in the organic solvent recovery tank 20 and the condensed water recovery tank 21, respectively. In addition, as a condenser, it replaces with the said low temperature condenser 18, and a pressurized deep-cooling type | mold condenser etc. can also be used.

ここで、前記凝縮水回収タンク17、21に回収された凝縮水は、若干の有機溶剤を含有している。該有機溶剤を含有している凝縮水は、有機溶剤を除去する除去処理を行なった後に排水される。また、低温凝縮器18から排出されるガスは、必要に応じて活性炭等の吸着剤に吸着させて有機溶剤を除去処理してから、外部に排気される。   Here, the condensed water recovered in the condensed water recovery tanks 17 and 21 contains some organic solvent. The condensed water containing the organic solvent is drained after performing a removal treatment for removing the organic solvent. The gas discharged from the low temperature condenser 18 is adsorbed by an adsorbent such as activated carbon as necessary to remove the organic solvent, and then exhausted to the outside.

叙述の如く構成された本実施の形態において、脱着装置は、有機溶剤を吸着した活性炭が充填される脱着槽1と、該脱着槽1に加熱されたドライガスを供給するブロア2および加熱器3と、脱着槽1に過熱水蒸気を供給する過熱水蒸気発生装置6と、脱着槽1へのドライガス、過熱水蒸気の供給を切換えるための第一、第二開閉弁5、8とを備えている。そして、脱着槽1に充填された活性炭を脱着する場合には、まず、活性炭に加熱されたドライガスを供給して脱着する第一脱着工程が行なわれ、その後に、前記第一工程で脱着された活性炭に過熱水蒸気を供給して更に脱着する第二脱着工程が行なわれることになる。   In the present embodiment configured as described above, the desorption apparatus includes a desorption tank 1 filled with activated carbon that has adsorbed an organic solvent, a blower 2 that supplies heated dry gas to the desorption tank 1, and a heater 3. And a superheated steam generator 6 for supplying superheated steam to the desorption tank 1, and first and second on-off valves 5 and 8 for switching the supply of dry gas and superheated steam to the desorption tank 1. When the activated carbon filled in the desorption tank 1 is desorbed, first, a first desorption step is performed in which the activated gas is supplied to the activated carbon and desorbed, and then desorbed in the first step. A second desorption step is performed in which superheated steam is supplied to the activated carbon for further desorption.

而して、ドライガスを用いた第一脱着工程の後に、過熱水蒸気を用いた第二脱着工程が行なわれることになり、これにより、ドライガスを用いた第一脱着工程では脱着されずに活性炭に残存している有機溶剤を、過熱水蒸気を用いた第二脱着工程によって確実に脱着できることになって、高い脱着率を確保できる。しかも、過熱水蒸気を用いた第二脱着工程は、ドライガスを用いて脱着された後の活性炭に対して行なわれるため、ドライガスを用いた脱着を行なわずに過熱水蒸気を用いた脱着のみを行なう場合と比して、過熱水蒸気の使用量を大幅に低減することができる。この結果、脱着後の有機溶剤ガスと水蒸気との混合ガスを凝縮したときに生じる凝縮水を大幅に少なくすることができ、よって、凝縮水から有機溶剤を除去するための除去処理を小規模にすることができて、除去処理の容易化、コスト低減に大きく貢献できる。   Thus, after the first desorption step using the dry gas, the second desorption step using the superheated steam is performed, so that the activated carbon is not desorbed in the first desorption step using the dry gas. The organic solvent remaining in the substrate can be surely desorbed by the second desorption step using superheated steam, and a high desorption rate can be secured. Moreover, since the second desorption step using superheated steam is performed on the activated carbon after desorption using dry gas, only desorption using superheated steam is performed without performing desorption using dry gas. Compared with the case, the usage-amount of superheated steam can be reduced significantly. As a result, the condensed water generated when the mixed gas of the organic solvent gas and water vapor after desorption is condensed can be greatly reduced, and thus the removal process for removing the organic solvent from the condensed water can be reduced on a small scale. This can greatly contribute to the simplification of removal processing and cost reduction.

しかもこのものにおいて、第一脱着工程に用いられるドライガスを加熱するための加熱器3は、過熱水蒸気発生装置6が発生する過熱水蒸気を熱媒としているから、第二脱着工程に用いられる過熱水蒸気を有効利用して第一脱着工程に用いられるドライガスを加熱できることになって、ドライガス加熱用の熱源を別途必要とせず、装置の兼用化、省エネルギー化が図れる。   In addition, in this apparatus, the heater 3 for heating the dry gas used in the first desorption process uses the superheated steam generated by the superheated steam generator 6 as a heat medium, so the superheated steam used in the second desorption process. It is possible to heat the dry gas used in the first desorption process by effectively utilizing the above, so that a separate heat source for heating the dry gas is not required, and the apparatus can be shared and energy can be saved.

次に、本発明の有用性を確認するための予備実験例、実施例、比較例の各実験について、以下に具体的に記載する。これら予備実験例、実施例、比較例の各実験に用いた装置は、前述した脱着装置を実用化レベルよりも小型化したものであって、同一の符号を附すと共に、各装置の説明は省略する。また、これらの実験において、脱着槽1に充填される吸着剤としては活性炭を用い、該活性炭の13.8kgに有機溶剤としてトルエン(CCH)2.90kgを吸着させ、該トルエンを吸着した活性炭からトルエンを脱着させる実験を行った。 Next, preliminary experiments, examples and comparative examples for confirming the usefulness of the present invention will be specifically described below. The devices used in the experiments of these preliminary experimental examples, examples, and comparative examples are the above-described desorption devices downsized from the practical level, and are given the same reference numerals, and the description of each device is as follows. Omitted. In these experiments, activated carbon was used as the adsorbent filled in the desorption tank 1, and 2.90 kg of toluene (C 6 H 5 CH 3 ) as an organic solvent was adsorbed to 13.8 kg of the activated carbon. An experiment was conducted in which toluene was desorbed from the activated carbon adsorbed with.

<予備実験例>
予備実験として、本発明の第一脱着工程の脱着率が高くなる条件を検討するために、ドライガスの温度、風量をパラメータとして、ドライガスのみによる脱着を行なった。この場合に、ブロア2および加熱器3は、図2の実験No1−1〜No1−6に示す温度、風量の加熱空気を脱着槽1に供給するように設定した。この加熱空気による脱着は、脱着時間1時間で終了させた。その結果を図2に示すが、この予備実験で脱着率が最も高いのは実験No1−3(脱着量2.66kg、脱着率91%)であり、そこで、該実験No1−3の条件(加熱空気の温度207℃、風量800L/分)を、後述する実施例の第一脱着工程の条件として採用することにした。尚、実験No1−3の条件で脱着時期を1時間以上しても、トルエンの脱着量は殆ど増加しないことを実験により確認した。
<Example of preliminary experiment>
As a preliminary experiment, in order to examine the conditions for increasing the desorption rate in the first desorption process of the present invention, desorption was performed only with dry gas using the temperature and air volume of the dry gas as parameters. In this case, the blower 2 and the heater 3 were set so as to supply heated air having a temperature and an air volume shown in Experiments No. 1-1 to No. 1-6 in FIG. This desorption with heated air was completed after a desorption time of 1 hour. The results are shown in FIG. 2, and the highest desorption rate in this preliminary experiment is Experiment No. 1-3 (desorption amount 2.66 kg, desorption rate 91%). An air temperature of 207 ° C. and an air volume of 800 L / min) were adopted as conditions for the first desorption process of the examples described later. In addition, even if the desorption time was 1 hour or more under the conditions of Experiment No1-3, it was confirmed by experiments that the desorption amount of toluene hardly increased.

<実施例>
本発明の実施例として、ドライガスを用いた第一脱着工程の後に、過熱水蒸気を用いた第二工程を行なった。この場合に、第一脱着工程において、ブロア2および加熱器3は、207℃、800L/分(予備実験の実験No1−3の条件)の加熱空気を脱着槽1に供給するように設定すると共に、第一脱着工程は、脱着時間1時間で終了させた。前述した予備実験の結果から、第一脱着工程が終了した時点でのトルエンの脱着量は2.66kgであり、脱着率は91%である。また、第二脱着工程において、過熱水蒸気発生装置6は、図3の実験No2−1〜No2−3に示す温度、蒸気量の過熱水蒸気を脱着槽1に供給するように設定すると共に、第二脱着工程は、脱着槽1の出口側温度が120℃(トルエンの沸点110℃よりも10℃高い温度)を越えた時点で終了させた。その結果を図3に示すが、第二脱着工程で要した脱着時間は、実験No2−1は35分、実験No2−2は31分、実験No2−3は25分である。また、実験No2−1〜No2−3の何れにおいても、第二脱着工程が終了した時点でのトルエンの脱着量(第一脱着工程で脱着された分を含む)は2.90kgであり、脱着率は100%であった。
これにより、加熱空気(ドライガス)を用いた第一脱着工程の後に、過熱水蒸気を用いた第二脱着工程を行なうことによって、高い脱着率(実施例では100%)で脱着できることが確認された。この実施例で用いた過熱水蒸気の総量は、計算上、実験No2−1では25kg((43kg/時間)×35分=25kg)、実験No2−2では22kg((43kg/時間)×31分=22kg)、実験No2−3では20kg((47kg/時間)×25分=20kg)である。
<Example>
As an example of the present invention, a second step using superheated steam was performed after the first desorption step using dry gas. In this case, in the first desorption step, the blower 2 and the heater 3 are set so as to supply heated air of 207 ° C. and 800 L / min (conditions of the preliminary experiment No. 1-3) to the desorption tank 1. The first desorption step was completed with a desorption time of 1 hour. From the result of the preliminary experiment described above, the desorption amount of toluene at the time when the first desorption step is completed is 2.66 kg, and the desorption rate is 91%. In the second desorption process, the superheated steam generator 6 is set so as to supply the superheated steam having the temperature and the amount of steam shown in the experiments No2-1 to No2-3 in FIG. The desorption process was terminated when the outlet side temperature of the desorption tank 1 exceeded 120 ° C. (temperature higher by 10 ° C. than the boiling point of toluene 110 ° C.). The results are shown in FIG. 3, and the desorption time required in the second desorption step is 35 minutes for Experiment No2-1, 31 minutes for Experiment No2-2, and 25 minutes for Experiment No2-3. Moreover, in any of Experiment No2-1 to No2-3, the desorption amount of toluene (including the amount desorbed in the first desorption step) at the time when the second desorption step is completed is 2.90 kg, The rate was 100%.
Thereby, it was confirmed that the desorption can be performed with a high desorption rate (100% in the example) by performing the second desorption step using superheated steam after the first desorption step using heated air (dry gas). . In the calculation, the total amount of superheated steam used in this example is 25 kg ((43 kg / hour) × 35 minutes = 25 kg) in Experiment No2-1, and 22 kg ((43 kg / hour) × 31 minutes in Experiment No2-2). 22 kg) and 20 kg in Experiment No2-3 ((47 kg / hour) × 25 minutes = 20 kg).

<比較例>
比較例として、ドライガスによる脱着を行なわずに、過熱水蒸気による脱着のみを行なった。この場合に、過熱水蒸気発生装置6は、図4の実験No3−1〜No3−3に示す温度、蒸気量の過熱水蒸気を脱着槽1に供給するように設定したが、該実験No3−1〜No3−3で設定した過熱水蒸気の温度、蒸気量は、前記実施例の実験No2−1〜No2−3で設定した過熱水蒸気の温度、蒸気量とそれぞれ同一である。また、この過熱水蒸気による脱着は、実施例と同様に、脱着槽1の出口側温度が120℃(トルエンの沸点110℃よりも10℃高い温度)を越えた時点で終了させた。その結果を図4に示すが、比較例で要した脱着時間は、実験No3−1は91分、実験No3−2は80分、実験No3−3は65分である。また、実験No3−1〜No3−3の何れにおいても、トルエンの脱着量(第一脱着工程で脱着された分を含む)は2.9kgであり、脱着率は100%であった。また、この比較例で用いた過熱水蒸気の総量は、計算上、実験No3−1では65kg((43kg/時間)×91分=65kg)、実験No3−2では57kg((43kg/時間)×57分=57kg)、実験No3−3では51kg((47kg/時間)×65分=51kg)である。
このことから、過熱水蒸気による脱着のみを行なう比較例では、前記実施例と同様に、高い脱着率で脱着することはできるものの、実施例と比して、多量(約2.6倍)の過熱水蒸気を必要とすることが確認され、これにより、本発明が実施された実施例では、比較例と比して過熱水蒸気の使用量を大幅に低減できることが確認された。
<Comparative example>
As a comparative example, only desorption with superheated steam was performed without desorption with dry gas. In this case, the superheated steam generator 6 was set to supply the superheated steam having the temperature and the amount of steam shown in Experiments No. 3-1 to No. 3-3 in FIG. The temperature and the amount of steam of the superheated steam set in No3-3 are the same as the temperature and the amount of steam of the superheated steam set in Experiments No2-1 to No2-3 of the above embodiment. The desorption with superheated steam was terminated when the outlet side temperature of the desorption tank 1 exceeded 120 ° C. (temperature higher by 10 ° C. than the boiling point of toluene 110 ° C.), as in the example. The results are shown in FIG. 4, and the desorption time required for the comparative example is 91 minutes for Experiment No3-1, 80 minutes for Experiment No3-2, and 65 minutes for Experiment No3-3. Moreover, in any of Experiment No3-1 to No3-3, the desorption amount of toluene (including the amount desorbed in the first desorption step) was 2.9 kg, and the desorption rate was 100%. In addition, the total amount of superheated steam used in this comparative example was calculated to be 65 kg ((43 kg / hour) × 91 minutes = 65 kg) in Experiment No3-1 and 57 kg ((43 kg / hour) × 57 in Experiment No3-2. Min = 57 kg) and in Experiment No3-3, it is 51 kg ((47 kg / hour) × 65 min = 51 kg).
Therefore, in the comparative example in which only desorption with superheated steam is performed, desorption can be performed at a high desorption rate as in the above-described example, but a large amount (about 2.6 times) of overheating as compared with the example. It was confirmed that water vapor was required, and thus it was confirmed that the amount of superheated water vapor used can be significantly reduced in the examples in which the present invention is implemented as compared with the comparative example.

尚、前記実施例では、第一脱着工程で、該第一脱着工程で脱着できる最大量まで脱着し、第二脱着工程で残りの分を脱着するように設定した。この様にした場合には、第二脱着工程で脱着する残りの脱着量が最小となるため、過熱水蒸気の使用量を最大限低減できることになるが、これに限定されることなく、第一、第二の各工程で脱着する脱着量の割合は、第一、第二の各脱着工程で使用するエネルギーや水処理にかかるコスト等を総合的に考慮して適宜設定することができる。   In the above example, the first desorption process was set to desorb up to the maximum amount that can be desorbed in the first desorption process, and the remaining desorption was desorbed in the second desorption process. In this case, since the remaining desorption amount to be desorbed in the second desorption step is minimized, the amount of superheated steam used can be reduced to the maximum, but the first, The ratio of the desorption amount desorbed in each of the second steps can be appropriately set in consideration of the energy used in each of the first and second desorption steps, the cost for water treatment, and the like.

例えば、ドライガスによる第一脱着工程を、脱着効率の比較的高い時点で終了させるように設定することもできる。つまり、第一脱着工程の脱着効率(時間あたりの脱着量)は、脱着開始直後は高いが、脱着時間が経過するにつれて低下する。このため、第一脱着工程で脱着できる最大量まで脱着すると、脱着効率の低い状態での脱着時間が長くなって、省エネルギー化に反してしまう惧れがある。そこで、第一脱着工程は、脱着効率の比較的高い時点(例えば、吸着量の70%まで脱着した時点)で終了させ、残りを第二脱着工程で脱着するように設定しても良い。この場合においても、ドライガスを用いた脱着を行なわずに過熱水蒸気を用いた脱着のみを行なう場合と比して、過熱水蒸気の使用量を大幅に低減することができるのは勿論である。   For example, the first desorption step with dry gas can be set to be terminated at a time when the desorption efficiency is relatively high. That is, the desorption efficiency (desorption amount per hour) of the first desorption step is high immediately after the start of desorption, but decreases as the desorption time elapses. For this reason, if the maximum amount that can be desorbed in the first desorption step is desorbed, the desorption time in a state where the desorption efficiency is low becomes long, which may be contrary to energy saving. Therefore, the first desorption step may be set to be terminated when the desorption efficiency is relatively high (for example, when desorption is performed up to 70% of the adsorption amount) and the rest is desorbed in the second desorption step. Even in this case, it is a matter of course that the amount of superheated steam used can be greatly reduced as compared with the case where only desorption using superheated steam is performed without performing desorption using dry gas.

本発明は、活性炭やゼオライト等の吸着剤に吸着された有機溶剤を脱着する場合に利用できる。   The present invention can be used when desorbing an organic solvent adsorbed on an adsorbent such as activated carbon or zeolite.

1 脱着槽
2 ブロア
3 加熱器
5 第一開閉弁
6 過熱水蒸気発生装置
8 第二開閉弁
DESCRIPTION OF SYMBOLS 1 Desorption tank 2 Blower 3 Heater 5 First on-off valve 6 Superheated steam generator 8 Second on-off valve

Claims (3)

有機溶剤を吸着した吸着剤から前記有機溶剤を脱着するための脱着方法であって、該脱着方法は、前記吸着剤にドライガスを供給して脱着する第一脱着工程と、該第一脱着工程で脱着された吸着剤に過熱水蒸気を供給して更に脱着する第二脱着工程とを備えることを特徴とする有機溶剤の脱着方法。   A desorption method for desorbing the organic solvent from an adsorbent adsorbing an organic solvent, the desorption method comprising a first desorption step of desorbing by supplying a dry gas to the adsorbent, and the first desorption step And a second desorption step of further desorption by supplying superheated steam to the adsorbent desorbed in step (b). 有機溶剤を吸着した吸着剤から前記有機溶剤を脱着するための脱着装置であって、該脱着装置は、前記有機溶剤を吸着した吸着剤が充填される脱着槽と、該脱着槽にドライガスを供給するドライガス供給手段と、脱着槽に過熱水蒸気を供給する過熱水蒸気供給手段と、前記ドライガスを供給して脱着する第一脱着工程の後に過熱水蒸気を供給して脱着する第二脱着工程を行なうべく脱着槽へのドライガス、過熱水蒸気の供給を切換える切換え手段とを備えて構成されることを特徴とする有機溶剤の脱着装置。   A desorption device for desorbing the organic solvent from an adsorbent adsorbing an organic solvent, the desorption device comprising: a desorption tank filled with an adsorbent adsorbing the organic solvent; and a dry gas in the desorption tank A dry gas supply means for supplying; a superheated steam supply means for supplying superheated steam to the desorption tank; and a second desorption process for supplying and desorbing superheated steam after the first desorption process of supplying and desorbing said dry gas. An organic solvent desorption apparatus comprising: a switching means for switching the supply of dry gas and superheated steam to the desorption tank. 請求項2において、ドライガス供給手段は、脱着槽に供給されるドライガスを加熱する加熱器を含むと共に、該加熱器は、過熱水蒸気供給手段が発生する過熱水蒸気を熱媒としてドライガスを加熱する構成であることを特徴とする有機溶剤の脱着装置。   3. The dry gas supply means according to claim 2, wherein the dry gas supply means includes a heater that heats the dry gas supplied to the desorption tank, and the heater heats the dry gas using the superheated steam generated by the superheated steam supply means as a heat medium. An organic solvent desorption apparatus characterized by comprising:
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CN105758699A (en) * 2016-03-01 2016-07-13 宁波市机电工业研究设计院有限公司 Solvent desorbing device and determination method thereof
CN109731433A (en) * 2018-12-18 2019-05-10 杭州捷瑞空气处理设备有限公司 The ethyl acetate recovery method combined is adsorbed with runner using activated carbon adsorption
CN113758266A (en) * 2020-06-05 2021-12-07 株式会社岛津制作所 Degreasing furnace and degreasing method
CN114322558A (en) * 2020-09-29 2022-04-12 株式会社岛津制作所 Degreasing furnace and degreasing method

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105758699A (en) * 2016-03-01 2016-07-13 宁波市机电工业研究设计院有限公司 Solvent desorbing device and determination method thereof
CN109731433A (en) * 2018-12-18 2019-05-10 杭州捷瑞空气处理设备有限公司 The ethyl acetate recovery method combined is adsorbed with runner using activated carbon adsorption
CN113758266A (en) * 2020-06-05 2021-12-07 株式会社岛津制作所 Degreasing furnace and degreasing method
CN114322558A (en) * 2020-09-29 2022-04-12 株式会社岛津制作所 Degreasing furnace and degreasing method

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