JPS6218207B2 - - Google Patents
Info
- Publication number
- JPS6218207B2 JPS6218207B2 JP54031703A JP3170379A JPS6218207B2 JP S6218207 B2 JPS6218207 B2 JP S6218207B2 JP 54031703 A JP54031703 A JP 54031703A JP 3170379 A JP3170379 A JP 3170379A JP S6218207 B2 JPS6218207 B2 JP S6218207B2
- Authority
- JP
- Japan
- Prior art keywords
- adsorption
- adsorption tank
- raw gas
- desorption
- exhaust gas
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 238000001179 sorption measurement Methods 0.000 claims description 123
- 238000000034 method Methods 0.000 claims description 59
- 239000002904 solvent Substances 0.000 claims description 42
- 238000003795 desorption Methods 0.000 claims description 37
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 34
- 238000001816 cooling Methods 0.000 claims description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 27
- 238000002336 sorption--desorption measurement Methods 0.000 claims description 5
- 230000008929 regeneration Effects 0.000 claims description 3
- 238000011069 regeneration method Methods 0.000 claims description 3
- 239000007789 gas Substances 0.000 description 93
- 239000000779 smoke Substances 0.000 description 17
- 238000001035 drying Methods 0.000 description 16
- 238000011084 recovery Methods 0.000 description 11
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 6
- 230000000694 effects Effects 0.000 description 3
- 230000002411 adverse Effects 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000000112 cooling gas Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000006073 displacement reaction Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 150000002576 ketones Chemical class 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
Description
【発明の詳細な説明】
本発明は活性炭による溶剤回収装置の吸脱着方
法の改良に関し、更に詳しくは再生脱着工程終了
後の高温、高湿の吸着槽を、吸着工程に切替える
初期に発生する溶剤を含む白煙と水滴の飛散を防
止した吸脱着方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in the adsorption/desorption method of a solvent recovery device using activated carbon. The present invention relates to an adsorption/desorption method that prevents white smoke and water droplets from scattering.
2槽あるいは多槽からなる固定層型活性炭吸着
槽を使用して原ガス中の溶剤を吸着し、次いで活
性炭層に水蒸気を通じて吸着された溶剤を脱着回
収する方法及び装置は多数知られている。これら
の溶剤回収装置は基本的に吸着工程、脱着工程、
乾燥工程、冷却工程、及び溶剤精製工程からな
る。上記工程のうち乾燥と冷却の装置は送風機、
加熱器、弁、ダクトで構成され、脱着終了後の吸
着槽にかなり多量の加熱空気を通じて活性炭層の
水分を乾燥し、次いで冷風に切り換えて冷却を行
なうもので、処理風量が大きいためかなりの設備
費及び運転費を要し、又操作が煩雑になる。 Many methods and devices are known for adsorbing a solvent in raw gas using a fixed-bed activated carbon adsorption tank consisting of two tanks or multiple tanks, and then desorbing and recovering the adsorbed solvent by passing water vapor into the activated carbon layer. These solvent recovery devices basically handle the adsorption process, desorption process,
It consists of a drying process, a cooling process, and a solvent purification process. In the above process, the drying and cooling equipment is a blower,
It consists of a heater, valves, and ducts, and after desorption is completed, a fairly large amount of heated air is passed through the adsorption tank to dry the moisture in the activated carbon layer, and then the activated carbon layer is cooled by switching to cold air.Because the processing air volume is large, it requires considerable equipment. This requires additional costs and operating costs, and the operation becomes complicated.
しかしこの乾燥・冷却工程を省略しても溶剤の
回収率に実質的な悪影響を与えないことから、近
時この乾燥、冷却工程を省略することが一般に行
なわれている。しかしながら、一般の溶剤回収装
置では脱着工程終了直後の活性炭吸着層は水蒸気
による脱着のために、吸着槽内は水蒸気で飽和
し、使用活性炭量の約40〜50wt%の水分を含
み、約100℃の高温状態に保たれているので、従
来法のように乾燥、冷却工程を行なつた場合でも
乾燥工程開始直後の数分間はげしい白煙を発生
し、その凝縮による水滴を装置の周辺に撒き散ら
した。まして最近のように乾燥冷却を省略した吸
着方法では、高温の吸着槽に溶剤の入つたガスが
入るので白煙や水滴の外に、とくに破過する溶剤
濃度は大きく問題であつた。この白煙発生を含む
弊害は公害上の見地から改善が切望されている。 However, since omitting this drying/cooling step does not have a substantial adverse effect on the recovery rate of the solvent, it has recently become common practice to omit this drying/cooling step. However, in general solvent recovery equipment, the activated carbon adsorption layer immediately after the desorption process is desorbed by water vapor, so the inside of the adsorption tank is saturated with water vapor, contains about 40 to 50 wt% of water based on the amount of activated carbon used, and has a temperature of about 100°C. Because the drying and cooling process is carried out as in the conventional method, intense white smoke is generated for several minutes immediately after the start of the drying process, and water droplets from the condensation are scattered around the equipment. Ta. Furthermore, with the recent adsorption methods that omit drying and cooling, gas containing solvent enters the high-temperature adsorption tank, so in addition to white smoke and water droplets, breakthrough solvent concentration has been a major problem. There is a strong need to improve these negative effects, including the generation of white smoke, from a pollution standpoint.
本発明は従来の溶剤回収装置に簡単な機構を付
設することによつて、再生直後の吸着槽に原ガス
を通じ、活性炭層の減湿と冷却を行うことによつ
て惹き起される上記欠点を一挙に解決する産業上
有利な吸着方法の提供を目的とする。 The present invention solves the above-mentioned drawbacks caused by dehumidifying and cooling the activated carbon layer by passing the raw gas to the adsorption tank immediately after regeneration by adding a simple mechanism to the conventional solvent recovery device. The purpose is to provide an industrially advantageous adsorption method that solves all problems at once.
本発明は通常の吸着工程の所要時間に比して脱
着工程の所要時間は約1/2であり、次の吸着工程開
始迄に充分の余裕時間があり、又この脱着から吸
着への切替時の高濃度溶剤、及び水滴を伴うはげ
しい白煙発生時間は初期の3〜4分間に過ぎない
こと、及び水蒸気を含むかなり熱いガスを予定の
吸着工程を半ば終了した水分が蒸発し、温度の下
つている別の吸着槽に少量導入しても吸着帯の移
動は僅かであり、溶剤の破過は実質的に生じない
と云う知見から本発明を完成した。 In the present invention, the time required for the desorption process is approximately 1/2 of the time required for a normal adsorption process, and there is sufficient time before the start of the next adsorption process, and when switching from desorption to adsorption, The generation time of heavy white smoke accompanied by highly concentrated solvents and water droplets is only the initial 3 to 4 minutes, and the fact that the water vapor that has completed the planned adsorption process halfway through the intended adsorption process is caused by the fact that the water vapor evaporates and the temperature decreases. The present invention was completed based on the knowledge that even if a small amount of solvent is introduced into another adsorption tank, the movement of the adsorption zone is slight and there is virtually no breakthrough of the solvent.
本発明の特徴は、水蒸気による脱着工程終了後
の吸着槽に、吸着工程続行中のあるいは終了直前
の他方の吸着槽に導入されている原ガスの全部、
若しくは一部を弁の開度調節によつてこの脱着工
程終了後の吸着槽に通した後の排ガスを、そのま
まあるいは冷却したのち、他の正規の吸着工程中
のあるいは終了直前の吸着槽を通して、上部より
排出し、次いで所定時間経過後、弁を切替えて脱
着工程終了後の吸着槽を次の吸着工程開始のため
に待機状態とするか、あるいは脱着工程終了後の
吸着槽を待機させずに続いて吸着工程に切替える
ことからなる。このように原ガスを脱着工程終了
後の吸着槽に所定時間、所定風量を通じ、その排
出ガスを他の吸着槽を一旦通して排出することに
より、高温で水分の多い吸着槽は冷却減湿され、
吸着工程切替え時の初期の白煙発生、高濃度溶剤
の放出は防止される。 A feature of the present invention is that all of the raw gas introduced into the adsorption tank after the completion of the water vapor desorption process and into the other adsorption tank during the adsorption process or just before the completion of the adsorption process,
Or, by adjusting the opening degree of the valve, the exhaust gas after passing through the adsorption tank after the completion of the desorption process is passed as it is or after being cooled, and then passed through the adsorption tank during or just before the completion of another regular adsorption process, Discharge from the upper part, and then after a predetermined period of time, switch the valve to make the adsorption tank after the desorption process stand by for the start of the next adsorption process, or do not leave the adsorption tank after the desorption process on standby for the start of the next adsorption process. Subsequently, it consists of switching to an adsorption step. In this way, the raw gas is passed through the adsorption tank for a predetermined period of time at a predetermined air volume after the desorption process is completed, and the exhaust gas is discharged through another adsorption tank, thereby cooling and dehumidifying the high-temperature, moisture-rich adsorption tank. ,
The initial generation of white smoke and release of highly concentrated solvents at the time of switching the adsorption process are prevented.
次に本願の構成及び作用を図を用いて説明す
る。第1図は2槽式の吸着装置に本発明を適用し
た原理的な実施例である。第1図に於いて通常の
吸着方法として回収されるべき溶剤を含む原ガス
は、原ガスブロワー3によりガス冷却器4で原ガ
ス中の水分を凝縮、分離したのち、通常20〜30℃
の温度で弁21から吸着槽1に入り吸着槽1内の
活性炭層で溶剤を吸着したのち排ガスは弁22よ
り排出管11を経て大気に放出される。この吸着
工程の所要時間は、装置の型式や吸着すべき溶剤
の種類量などによつて異なるが通常は約1時間で
ある。吸着槽1が吸着工程を開始すると、既に吸
着工程を完了している他方の吸着槽2の脱着工程
が続いて始まる。吸着槽2の脱着工程は吸着槽2
内の活性炭層に吸着された溶剤を水蒸気によつて
追い出す工程である。 Next, the configuration and operation of the present application will be explained using figures. FIG. 1 shows a principle embodiment in which the present invention is applied to a two-tank adsorption device. In Fig. 1, the raw gas containing the solvent to be recovered in a normal adsorption method is heated to 20 to 30°C after condensing and separating the moisture in the raw gas in the gas cooler 4 using the raw gas blower 3.
The exhaust gas enters the adsorption tank 1 through the valve 21 at a temperature of 22. After the solvent is adsorbed by the activated carbon layer in the adsorption tank 1, the exhaust gas is discharged from the valve 22 through the exhaust pipe 11 to the atmosphere. The time required for this adsorption step varies depending on the type of device, the type and amount of solvent to be adsorbed, etc., but is usually about 1 hour. When the adsorption tank 1 starts the adsorption process, the desorption process of the other adsorption tank 2, which has already completed the adsorption process, starts subsequently. The desorption process of adsorption tank 2
This is a process in which the solvent adsorbed on the activated carbon layer inside the tank is expelled by steam.
この操作は先ず弁19が開き、次いで蒸気弁1
6が開いて水蒸気導管6より吸着槽2内に水蒸気
を導入する。水蒸気圧力は脱着すべき溶剤の種類
や装置の大きさによつて異なるがゲージ圧で通常
2〜8Kg/cm2の水蒸気が用いられる。吸着槽2に
水蒸気が導入されると水蒸気による熱と置換によ
つて活性炭層に吸着されていた溶剤は追い出され
て水蒸気と一緒に凝縮冷却器で凝縮し、冷却され
てデカンター9に至り、ここで分液され、上層の
溶剤と下層の微量の溶剤を溶解する水は夫々次の
精製工程に送られて別途処理される。 This operation first opens the valve 19, then the steam valve 1.
6 opens to introduce water vapor into the adsorption tank 2 from the water vapor conduit 6. Although the steam pressure varies depending on the type of solvent to be desorbed and the size of the apparatus, steam at a gauge pressure of 2 to 8 kg/cm 2 is usually used. When water vapor is introduced into the adsorption tank 2, the solvent adsorbed on the activated carbon layer is driven out by heat and displacement by the water vapor, condenses together with the water vapor in a condensing cooler, is cooled, and reaches a decanter 9, where it is The water that dissolves the solvent in the upper layer and the trace amount of solvent in the lower layer is sent to the next purification step and treated separately.
この脱着工程の所要時間は吸着工程のそれの約
1/2であり、通常の1時間の吸着に対して脱着の
所要時間は30分である。それ故吸着槽2が次の吸
着を開始するまで約30分の休止時間がある。2槽
以上の吸着槽からなる通常の溶剤回収装置では、
上記のような吸着と脱着の工程を交互に又は順次
に繰返す。 The time required for this desorption step is approximately that of the adsorption step.
1/2, and the time required for desorption is 30 minutes compared to the usual 1 hour adsorption. Therefore, there is a downtime of about 30 minutes before the adsorption tank 2 starts the next adsorption. In a normal solvent recovery device consisting of two or more adsorption tanks,
The adsorption and desorption steps as described above are repeated alternately or sequentially.
上述のように脱着工程を終了した吸着槽2は次
の脱着工程を開始する迄のこの休止時間を利用し
て乾燥と冷却を行なうことが以前は行なわれてい
たが、溶剤の回収率と吸着現象そのものに実質的
な悪影響がないことから、最近の溶剤回収装置で
は、コストの関係から、この乾燥、冷却工程を省
略することが行なわれている。乾燥、冷却の工程
はブロワーガス加熱器、ダクト、弁を吸着系統と
別途に設けダクトの口径が大きく、従つて、建設
費と維持費が装置全体のコストに対してかなり比
率を占めるものである。更にこの乾燥、冷却工程
を行なつた場合でも乾燥工程開始の初期2〜3分
間ははげしい白煙を放出する。これは吸着工程を
終了した直後の吸着槽に水蒸気が充満し、且つ内
部の活性炭層が水分を多量に含んでいるため乾燥
のために導入される熱風によつて、水蒸気や水分
が追い出されるためである。 Previously, the adsorption tank 2, which had completed the desorption process as described above, was used to dry and cool down during the downtime before starting the next desorption process. Since there is no substantial adverse effect on the phenomenon itself, recent solvent recovery apparatuses omit the drying and cooling steps due to cost considerations. The drying and cooling process requires a blower gas heater, duct, and valve to be installed separately from the adsorption system, and the diameter of the duct is large, so the construction and maintenance costs account for a large proportion of the overall equipment cost. . Furthermore, even when this drying and cooling process is carried out, intense white smoke is emitted for the first 2 to 3 minutes after the start of the drying process. This is because the adsorption tank is filled with water vapor immediately after the adsorption process is completed, and the activated carbon layer inside contains a large amount of water, so the hot air introduced for drying drives out the water vapor and water. It is.
一方、乾燥、冷却工程を省略した場合は、脱着
工程終了後約30分間休止して次の吸着工程を開始
するが、吸着槽はかなり容積が大きく30分間の放
置では殆んど冷却されない。従つて当然吸着工程
の開始にあたつてはげしい白煙を発生する。 On the other hand, if the drying and cooling steps are omitted, the next adsorption step will be started after a pause of about 30 minutes after the desorption step is completed, but the adsorption tank has a fairly large volume and will hardly be cooled if left for 30 minutes. Naturally, therefore, heavy white smoke is generated at the beginning of the adsorption process.
この際の白煙は前述の乾燥工程開始時の白煙に
比して量、質ともに異なる。乾燥用の熱風は比較
的温度が高く且つ溶剤を含まないが、乾燥、冷却
工程を省略して吸着を行なう場合は導入される原
ガスは常温に近いので白煙の量も稍多く又吸着槽
が冷却する迄原ガスに含まれる溶剤は吸着され
ず、活性炭層を破過して大気に放出される傾向が
あり、瞬間的には原ガス中の溶剤濃度と排出ガス
の溶剤濃度が殆んど等しくなる。このように排ガ
ス中に溶剤が存在する時間と濃度は白煙を発生す
る時間とその濃度に略比例する。この白煙発生時
間は3〜4分間であり、やがて時間の軽過と共に
吸着槽は冷却して正常の吸着に復帰する。このよ
うな排ガスが原ガス中の溶剤濃度に近い溶剤を排
出する時間はごく僅かであるので、全体的な溶剤
回収率に与える影響は実質的に少ない。 The white smoke at this time is different in quantity and quality from the white smoke at the start of the drying process described above. The hot air for drying has a relatively high temperature and does not contain any solvent, but if the drying and cooling steps are omitted and adsorption is performed, the raw gas introduced is close to room temperature, so the amount of white smoke is quite large, and the adsorption tank The solvent contained in the raw gas is not adsorbed until it cools down, and tends to break through the activated carbon layer and be released into the atmosphere, and momentarily the solvent concentration in the raw gas and the solvent concentration in the exhaust gas are almost the same. It becomes equal. As described above, the time and concentration of the solvent in the exhaust gas are approximately proportional to the time and concentration of white smoke generation. The white smoke generation time is 3 to 4 minutes, and as time passes, the adsorption tank cools down and returns to normal adsorption. Since such exhaust gases have a very short time to discharge solvent close to the concentration of solvent in the raw gas, the impact on the overall solvent recovery rate is substantially small.
以上のような工程が従来の一般的溶剤回収装置
では行なわれている。併し溶剤や水滴を含む白煙
の発生は公害防止の見地から望ましくなく、又最
近ケトン類やTHFの如き高価な溶剤の回収には
とくに僅かな回収率の向上も考慮されるようにな
つた。こゝに於いて本発明は簡単な設備を付設す
ることによつて、上記問題を解決した。即ち第1
図に於いて、今吸着槽1が吸着工程を同時に吸着
槽2が脱着工程を開始して30分を経過したとす
る。設定した吸着時間を60分とすると、吸着槽1
は吸着工程を半ば終了して水分蒸発のためにかな
り冷却し、吸着槽2は脱着工程を丁度終了したこ
とになる。吸着槽1内の活性炭量は所定の溶剤を
吸着するに必要な量の3倍程度の充分な吸着余裕
をもつて設計されているから、吸着開始30分後で
は吸着帯の溶剤濃度の極く稀薄な先端は吸着槽1
内の活性炭層下部の1/3に達する程度で、残りの
上部2/3は殆んど吸着に使われていない。このよ
うに吸着槽1が吸着工程を半ば終了し、吸着槽2
が脱着工程を開始して30分経過したときの弁の状
態は原ガス21、排気弁22は夫々開、蒸気弁1
6、脱着蒸気弁19、は夫々開であり、その他の
弁は全て閉である。次いで吸着槽1の状態はその
まゝで吸着槽2は脱着工程を終了する。即ち蒸気
弁16、脱着蒸気弁19は順次閉となる。次いで
吸着槽2に本発明の冷却工程を行なう。 The steps described above are performed in conventional general solvent recovery equipment. However, the generation of white smoke containing solvents and water droplets is undesirable from the standpoint of pollution prevention, and recently, even a slight improvement in the recovery rate has been considered, especially when recovering expensive solvents such as ketones and THF. . In this case, the present invention solves the above problem by adding simple equipment. That is, the first
In the figure, it is assumed that 30 minutes have passed since adsorption tank 1 started the adsorption process and adsorption tank 2 started the desorption process at the same time. If the set adsorption time is 60 minutes, adsorption tank 1
has halfway completed the adsorption process and has cooled considerably due to water evaporation, and the adsorption tank 2 has just completed the desorption process. The amount of activated carbon in the adsorption tank 1 is designed to have enough adsorption margin to be about three times the amount required to adsorb a given solvent. The thin tip is adsorption tank 1
The activated carbon layer only reaches the bottom 1/3 of the layer, and the remaining top 2/3 is hardly used for adsorption. In this way, adsorption tank 1 has halfway completed the adsorption process, and adsorption tank 2
30 minutes after starting the desorption process, the valve states are raw gas 21, exhaust valve 22 open, and steam valve 1.
6 and desorption steam valves 19 are open, and all other valves are closed. Next, the adsorption tank 2 completes the desorption process while the state of the adsorption tank 1 remains the same. That is, the steam valve 16 and the desorption steam valve 19 are closed in sequence. Next, the adsorption tank 2 is subjected to the cooling process of the present invention.
このために第1図に示すように冷却排ガス導管
12,13及び冷却排ガス弁17,18からなる
冷却排ガスの導入径路を配設する。脱着工程終了
後の吸着槽2の冷却のために冷却排ガス弁17,
18及び原ガス弁20を順次開とする。このよう
にして吸着槽2に原ガスを通じると原ガス中の溶
剤は吸着され冷却排ガスは吸着槽2内の活性炭層
の水分を奪いこの蒸発によつて吸着槽2は次第に
冷却する。吸着槽2に通じる原ガス量は白煙発生
の時間から原ガス量の約1/15程度で充分目的を達
する。この操作を行なうために吸着槽1の原ガス
弁21を全閉して、約4分間吸着槽2に原ガスを
通じて吸着槽2で吸着と冷却を行ないこの水分と
熱を有するガスを吸着槽1を通して排気管11よ
り大気に排出する。 For this purpose, as shown in FIG. 1, a cooling exhaust gas introduction path consisting of cooling exhaust gas conduits 12, 13 and cooling exhaust gas valves 17, 18 is provided. A cooling exhaust gas valve 17 for cooling the adsorption tank 2 after the desorption process is completed;
18 and raw gas valve 20 are sequentially opened. When the raw gas is passed through the adsorption tank 2 in this manner, the solvent in the raw gas is adsorbed, and the cooled exhaust gas removes moisture from the activated carbon layer in the adsorption tank 2, and the adsorption tank 2 is gradually cooled by this evaporation. The amount of raw gas flowing into the adsorption tank 2 is approximately 1/15 of the amount of raw gas from the time when white smoke is generated, which is sufficient to achieve the purpose. To perform this operation, the raw gas valve 21 of the adsorption tank 1 is fully closed, the raw gas is passed into the adsorption tank 2 for about 4 minutes, and the adsorption tank 2 adsorbs and cools the gas, which has moisture and heat. It is discharged to the atmosphere through the exhaust pipe 11.
この際に冷却排ガス導管13の途中にガス冷却
器(図示せず)を設けてこの冷却排ガス中の水分
を凝縮分離し、ガス冷却を行なうことも出来る。
このように吸着槽2に所定時間、全量の原ガスを
通じたのち、冷却排ガスを吸着槽1を通して排気
管11から排気するかわりに原ガス弁21を全閉
せずに適宜の開度に開き、原ガス弁20は全開又
は適宜の開度に調節して吸着槽1と吸着槽2の両
方例えば原ガス流量比で約15:2になるように、
同時に原ガスを通じ、吸着槽2を冷却した冷却排
ガスは同じく冷却排ガス導管12,13,14を
通して原ガス弁21から入る原ガスに合して吸着
槽1で吸着を行ない排気弁11から大気に放出す
ることも出来る。この際も前記と同様に冷却排ガ
ス導管13の途中にガス冷却器(図示せず)を設
けることが出来る。 At this time, a gas cooler (not shown) may be provided in the middle of the cooled exhaust gas conduit 13 to condense and separate moisture in the cooled exhaust gas, thereby performing gas cooling.
After passing the entire amount of raw gas to the adsorption tank 2 for a predetermined time in this way, instead of exhausting the cooled exhaust gas through the adsorption tank 1 and from the exhaust pipe 11, the raw gas valve 21 is opened to an appropriate opening degree without fully closing. The raw gas valve 20 is fully opened or adjusted to an appropriate opening so that both the adsorption tank 1 and the adsorption tank 2 have a raw gas flow rate ratio of about 15:2, for example.
At the same time, the cooled exhaust gas that has cooled the adsorption tank 2 through the raw gas is adsorbed in the adsorption tank 1 together with the raw gas that enters from the raw gas valve 21 through the cooled exhaust gas conduits 12, 13, and 14, and is released into the atmosphere from the exhaust valve 11. You can also do that. In this case as well, a gas cooler (not shown) can be provided in the middle of the cooling exhaust gas conduit 13 in the same manner as described above.
以上の2つの方法のうち後者即ち同時に2つの
吸着槽1,2に並列に原ガスを通じることは冷却
排ガス導管12〜14、弁17,18及び冷却器
(図示せず)が小さくなつてとくに有利であり、
原ガス量の比が上記比率の場合に最も小さく出来
る。上記2方法のいづれの場合も、一回のサイク
ルで吸着層1に入るべき規定の原ガス総量の約1/
15の量の原ガスを吸着槽2に通したあとは、吸着
槽1は正規の吸着工程に復帰し、吸着槽2は次の
吸着工程に切替えのために待機する。この冷却工
程を行なつても最初に設定した吸着、脱着のタイ
ムスケジユールは狂を生じることはなく、排ガス
中に白煙の発生や溶剤の破過を来すことはない。 Of the above two methods, the latter, that is, simultaneously passing the raw gas in parallel to the two adsorption tanks 1 and 2, is particularly advantageous because the cooling exhaust gas pipes 12 to 14, the valves 17 and 18, and the cooler (not shown) are smaller. advantageous;
The ratio of raw gas amounts can be minimized when the above ratio is achieved. In both of the above two methods, about 1/1/2 of the specified total amount of raw gas that should enter the adsorption layer 1 in one cycle.
After passing 15 of the raw gas through the adsorption tank 2, the adsorption tank 1 returns to the normal adsorption process, and the adsorption tank 2 waits for switching to the next adsorption process. Even if this cooling step is carried out, the initially set adsorption and desorption time schedule will not be disrupted, and no white smoke will be generated in the exhaust gas or solvent will break through.
第2図は本発明の他の実施例である。吸着槽
1,2に按分された原ガスの内脱着工程を終了し
た吸着槽2を通過した原ガスからの水蒸気や水滴
を含む排ガスは、冷却排ガス導管12,13の先
から原ガスブロワー3の吸引側に送られ、他の原
ガスと合一して原ガス冷却器4を通つて水分を凝
縮し、冷却したのち吸着槽1及び吸着槽2の両方
に同時に再び按分されて送られるように構成され
る。その他については第1図の実施例と同様であ
る。この場合も冷却ガス導管13の途中にガス冷
却器(図示せず)を設けることは有益である。第
2図の工程を用いると吸着槽2を通過したあとの
冷却排ガス導管は単純化される。 FIG. 2 shows another embodiment of the invention. The exhaust gas containing water vapor and water droplets from the raw gas that has passed through the adsorption tank 2 that has completed the desorption process and is divided into the adsorption tanks 1 and 2 in proportion is transferred from the end of the cooling exhaust gas conduits 12 and 13 to the raw gas blower 3. It is sent to the suction side, combined with other raw gas, passed through the raw gas cooler 4 to condense moisture, and after being cooled, it is proportionally distributed again and sent to both the adsorption tank 1 and the adsorption tank 2 at the same time. configured. The rest is the same as the embodiment shown in FIG. In this case as well, it is advantageous to provide a gas cooler (not shown) in the middle of the cooling gas conduit 13. Using the process shown in FIG. 2 simplifies the cooling exhaust gas conduit after passing through the adsorption tank 2.
第3図は吸着槽2を通過する冷却排ガスを冷却
排ガス導管12,13を経て、既設の脱着蒸気導
管7、凝縮冷却器8及びデカンター9を通して原
ガスブロワー3に循環する実施例を示すものであ
る。この場合は既設の脱着蒸気導管7、凝縮冷却
器8等によつてガス流速は規制され、全量の原ガ
スを通すことは出来ない。遮断弁24は吸着槽1
或いは2の冷却工程中のみ開いて、それ以外は閉
とする。その他の一般的な説明は図1,2の場合
と同様である。 FIG. 3 shows an embodiment in which the cooled exhaust gas passing through the adsorption tank 2 is circulated through the cooled exhaust gas conduits 12 and 13, the existing desorption vapor conduit 7, the condensing cooler 8 and the decanter 9 to the raw gas blower 3. be. In this case, the gas flow rate is regulated by the existing desorption steam conduit 7, condensing cooler 8, etc., and it is not possible to pass the entire amount of raw gas. The cutoff valve 24 is connected to the adsorption tank 1
Alternatively, it may be opened only during the cooling step 2 and closed at other times. Other general explanations are the same as those in FIGS. 1 and 2.
上述の説明に於いて再生脱着後の吸着槽2に通
すべき冷却用の原ガスは原理的には全量の原ガス
を通すことが出来るが、冷却の目的からは原ガス
全量の約1/12〜1/15を通すことで目的は達成さ
れるの
で、前述の次の吸着開始迄の余裕時間内に冷却が
完了するような少ない流量を用いる方が有利であ
る。このガス流量は例えばトルエン50Kg/Hの回
収にあたり、原ガス濃度を0.5Vol%とすると原ガ
スの全量は2620m3(20℃)/Hとなりトルエン蒸
気を除いた空気は2600m3(20℃)/Hとなるの
で、この場合冷却用の原ガスとして180〜200m3
(20℃)を約30分間に通せばよい。このようにし
て導管径や弁を小さくして設備のコストを下げ吸
着槽2を出た冷却排ガス用のガス冷却器を不必要
と、又図2及3に於ける原ガス冷却器4や凝縮冷
却器8の負荷を小さく出来る。又弁17,17′
あるいは18,18′はまとめて夫々一個の切替
弁とすることも出来る。 In the above explanation, in principle, the entire amount of raw gas for cooling to be passed through the adsorption tank 2 after regeneration and desorption can be passed through, but for the purpose of cooling, approximately 1/12 of the total amount of raw gas is required. Since the objective is achieved by passing ~1/15, it is advantageous to use a small flow rate that allows cooling to be completed within the above-mentioned margin time until the start of the next adsorption. This gas flow rate is, for example, when recovering 50 kg/H of toluene, and if the raw gas concentration is 0.5 Vol%, the total amount of raw gas is 2620 m 3 (20°C)/H, and the air excluding toluene vapor is 2600 m 3 (20°C)/H. H, so in this case, 180 to 200 m 3 is used as the raw gas for cooling.
(20℃) for about 30 minutes. In this way, the diameter of the conduit and the valve can be reduced to reduce the cost of the equipment and eliminate the need for a gas cooler for the cooled exhaust gas exiting the adsorption tank 2. The load on the condensing cooler 8 can be reduced. Also valves 17, 17'
Alternatively, 18 and 18' can be combined into one switching valve.
以上のように本発明によれば簡単な設備の付設
によつて容易な操作で溶剤回収装置の吸着開始時
に発生する高濃度溶剤の破過、白煙及び水滴の大
気への放出を防止することが出来て産業上又環境
保護の立場から極めて有益である。 As described above, according to the present invention, it is possible to prevent the breakthrough of highly concentrated solvent and the release of white smoke and water droplets into the atmosphere that occur when the solvent recovery device starts adsorption by installing simple equipment and with easy operation. This is extremely beneficial from an industrial and environmental standpoint.
第1図は本発明の要点を示す実施例であり、第
2図は脱着工程終了後の吸着槽を通過した冷却排
ガスを原ガスブロワーの吸引側に導いて吸引冷却
したのち他の吸着槽に通して排気するように構成
した他の実施例であり、又第3図は脱着工程終了
後の吸着槽を通過した冷却排ガスを既設の凝縮冷
却器及びデカンターを通して原ガスブロワーの吸
引側に導いて吸引冷却したのち他の吸着槽に通し
て大気に排気するように構成した別の実施例であ
る。
1…吸着槽、2…吸着槽、3…原ガスブロワ
ー、4…原ガス冷却器、5…原ガス導管、6…水
蒸気導管、7…脱着蒸気導管、8…凝縮冷却器、
9…デカンター、10…排気管、11…排気管、
12…冷却排ガス導管、13…冷却排ガス導管、
14…冷却排ガス導管、15…排気弁、16…蒸
気弁、17…冷却排ガス弁、18…冷却排ガス
弁、19…脱着蒸気弁、20…原ガス弁、21…
原ガス弁、22…排気弁、23…冷却排ガス導
管、24…遮断弁。
Figure 1 shows an embodiment showing the main points of the present invention, and Figure 2 shows the cooled exhaust gas that has passed through the adsorption tank after the desorption process is completed, is guided to the suction side of the raw gas blower, cooled by suction, and then transferred to another adsorption tank. Another embodiment is shown in which the cooled exhaust gas that has passed through the adsorption tank after the desorption step is guided to the suction side of the raw gas blower through the existing condensing cooler and decanter. This is another embodiment in which the adsorbent is cooled by suction and then passed through another adsorption tank and exhausted to the atmosphere. 1... Adsorption tank, 2... Adsorption tank, 3... Raw gas blower, 4... Raw gas cooler, 5... Raw gas conduit, 6... Steam conduit, 7... Desorption vapor conduit, 8... Condensing cooler,
9...Decanter, 10...Exhaust pipe, 11...Exhaust pipe,
12...Cooled exhaust gas conduit, 13...Cooled exhaust gas conduit,
14... Cooled exhaust gas conduit, 15... Exhaust valve, 16... Steam valve, 17... Cooled exhaust gas valve, 18... Cooled exhaust gas valve, 19... Desorption steam valve, 20... Raw gas valve, 21...
Raw gas valve, 22...Exhaust valve, 23...Cooled exhaust gas conduit, 24...Shutoff valve.
Claims (1)
である気相中の溶剤を吸着し、次いで水蒸気を用
いて該吸着溶剤を脱着する操作を繰返す方法にお
いて、脱着再生した吸着槽に原ガスの少なくとも
一部を通して得られる排気の全部若しくは一部を
そのまゝあるいは冷却した後他の吸着槽に通して
から大気中に放散し、次いで切替えて通常量の排
気をそのまゝ大気中に放散することを特徴とする
吸脱着方法。 2 脱着再生した吸着槽に原ガスの少なくとも一
部を通して得られる排気の全てが他の吸着槽に送
られる特許請求の範囲第1項に記載する吸脱着方
法。 3 脱着再生した吸着槽に原ガスの一部を通して
得られる排気が原ガスブロワーの吸引側へ送ら
れ、原ガスと混合される特許請求の範囲第1項に
記載する吸脱着方法。[Scope of Claims] 1. Desorption and regeneration in a method that repeats an operation of adsorbing a solvent in a gas phase, which is a raw gas, using a plurality of activated carbon adsorption tanks in turn, and then desorbing the adsorbed solvent using water vapor. All or part of the exhaust gas obtained by passing at least a portion of the raw gas through one adsorption tank is passed through another adsorption tank as it is or after cooling, and is then dissipated into the atmosphere, and then switched to pass the normal amount of exhaust gas into the atmosphere. Well, it is an adsorption/desorption method characterized by dissipation into the atmosphere. 2. The adsorption/desorption method according to claim 1, wherein all of the exhaust gas obtained by passing at least a portion of the raw gas through the desorption and regenerated adsorption tank is sent to another adsorption tank. 3. The adsorption/desorption method according to claim 1, wherein the exhaust gas obtained by passing a part of the raw gas through the desorption and regenerated adsorption tank is sent to the suction side of the raw gas blower and mixed with the raw gas.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3170379A JPS55124523A (en) | 1979-03-20 | 1979-03-20 | Adsorbing and desorbing method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3170379A JPS55124523A (en) | 1979-03-20 | 1979-03-20 | Adsorbing and desorbing method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS55124523A JPS55124523A (en) | 1980-09-25 |
| JPS6218207B2 true JPS6218207B2 (en) | 1987-04-22 |
Family
ID=12338419
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3170379A Granted JPS55124523A (en) | 1979-03-20 | 1979-03-20 | Adsorbing and desorbing method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS55124523A (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE59402050D1 (en) * | 1993-11-18 | 1997-04-17 | Sebald U E | Process and plant for removing solvent vapors from exhaust air |
| JP4548891B2 (en) * | 2000-02-29 | 2010-09-22 | 東邦化工建設株式会社 | Organic solvent recovery method |
| JP5835662B2 (en) * | 2011-10-18 | 2015-12-24 | 株式会社栗本鐵工所 | Control method of volatile organic compound processing apparatus |
| JP6229267B2 (en) * | 2013-01-29 | 2017-11-15 | 東洋紡株式会社 | Gas processing apparatus and gas processing method |
-
1979
- 1979-03-20 JP JP3170379A patent/JPS55124523A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS55124523A (en) | 1980-09-25 |
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