JPH0732861B2 - Activated carbon regeneration method - Google Patents
Activated carbon regeneration methodInfo
- Publication number
- JPH0732861B2 JPH0732861B2 JP1214105A JP21410589A JPH0732861B2 JP H0732861 B2 JPH0732861 B2 JP H0732861B2 JP 1214105 A JP1214105 A JP 1214105A JP 21410589 A JP21410589 A JP 21410589A JP H0732861 B2 JPH0732861 B2 JP H0732861B2
- Authority
- JP
- Japan
- Prior art keywords
- activated carbon
- desorption
- steam
- temperature
- adsorption
- 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 - Fee Related
Links
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims description 88
- 238000011069 regeneration method Methods 0.000 title description 4
- 238000001179 sorption measurement Methods 0.000 claims description 70
- 238000003795 desorption Methods 0.000 claims description 59
- 239000002904 solvent Substances 0.000 claims description 42
- 238000000034 method Methods 0.000 claims description 26
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 26
- 238000001816 cooling Methods 0.000 claims description 13
- 238000009834 vaporization Methods 0.000 claims description 4
- 230000008016 vaporization Effects 0.000 claims description 4
- 230000001172 regenerating effect Effects 0.000 claims description 3
- 238000010793 Steam injection (oil industry) Methods 0.000 claims 1
- 238000007664 blowing Methods 0.000 claims 1
- 239000003245 coal Substances 0.000 description 40
- 239000007789 gas Substances 0.000 description 31
- 238000007254 oxidation reaction Methods 0.000 description 16
- 230000003647 oxidation Effects 0.000 description 13
- JHIVVAPYMSGYDF-UHFFFAOYSA-N cyclohexanone Chemical compound O=C1CCCCC1 JHIVVAPYMSGYDF-UHFFFAOYSA-N 0.000 description 10
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 9
- 238000007796 conventional method Methods 0.000 description 9
- 238000010438 heat treatment Methods 0.000 description 7
- ZWEHNKRNPOVVGH-UHFFFAOYSA-N 2-Butanone Chemical compound CCC(C)=O ZWEHNKRNPOVVGH-UHFFFAOYSA-N 0.000 description 6
- 230000007423 decrease Effects 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 5
- 238000009833 condensation Methods 0.000 description 4
- 230000005494 condensation Effects 0.000 description 4
- 239000000498 cooling water Substances 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 238000001704 evaporation Methods 0.000 description 4
- 230000008020 evaporation Effects 0.000 description 4
- 238000011084 recovery Methods 0.000 description 4
- 241001661006 Pepper cryptic virus 2 Species 0.000 description 3
- 230000003197 catalytic effect Effects 0.000 description 3
- 238000006116 polymerization reaction Methods 0.000 description 3
- 230000008929 regeneration Effects 0.000 description 3
- 229920006395 saturated elastomer Polymers 0.000 description 3
- 241001504982 Pepper cryptic virus 1 Species 0.000 description 2
- WNLRTRBMVRJNCN-UHFFFAOYSA-N adipic acid Chemical compound OC(=O)CCCCC(O)=O WNLRTRBMVRJNCN-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000009835 boiling Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 239000005453 ketone based solvent Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000003960 organic solvent Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 230000001629 suppression Effects 0.000 description 2
- PVGHQBCTMALNFO-UHFFFAOYSA-N 2-acetyl-3-oxobutanoic acid Chemical compound CC(=O)C(C(C)=O)C(O)=O PVGHQBCTMALNFO-UHFFFAOYSA-N 0.000 description 1
- NTIZESTWPVYFNL-UHFFFAOYSA-N Methyl isobutyl ketone Chemical compound CC(C)CC(C)=O NTIZESTWPVYFNL-UHFFFAOYSA-N 0.000 description 1
- UIHCLUNTQKBZGK-UHFFFAOYSA-N Methyl isobutyl ketone Natural products CCC(C)C(C)=O UIHCLUNTQKBZGK-UHFFFAOYSA-N 0.000 description 1
- 235000011037 adipic acid Nutrition 0.000 description 1
- 239000001361 adipic acid Substances 0.000 description 1
- OILAIQUEIWYQPH-UHFFFAOYSA-N cyclohexane-1,2-dione Chemical compound O=C1CCCCC1=O OILAIQUEIWYQPH-UHFFFAOYSA-N 0.000 description 1
- 238000007872 degassing Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007717 exclusion Effects 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 150000002576 ketones Chemical class 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 150000002978 peroxides Chemical class 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000013557 residual solvent Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 229920003002 synthetic resin Polymers 0.000 description 1
- 239000000057 synthetic resin Substances 0.000 description 1
- 230000007704 transition Effects 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は活性炭に吸着させた溶剤を水蒸気を用いて脱着
する際に、脱着圧力、温度より低い圧力、温度の水蒸気
を用いて活性炭層(以下炭層と称する)に含まれる空気
を水蒸気と置換してから脱着を行い、脱着終了後、炭層
を脱着圧力よりも低い圧力に保持し、活性炭に含まれて
いる水分の蒸発脱着熱により、その圧力における水蒸気
飽和温度迄炭層温度を低下させた後、溶剤の吸着を行う
活性炭再生方法に関する。DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention is directed to desorbing a solvent adsorbed on activated carbon with water vapor by using water vapor having a desorption pressure, a pressure lower than temperature and temperature. (Hereinafter referred to as a coal bed) is replaced with steam after degassing, and after the desorption is completed, the coal bed is maintained at a pressure lower than the desorption pressure, and by the heat of vaporization and desorption of water contained in activated carbon, The present invention relates to a method for regenerating activated carbon in which a coal bed temperature is lowered to a steam saturation temperature at a pressure and then a solvent is adsorbed.
各種プラスチック製品の製造工程や磁気テープ工業等の
各種操作に伴って発生する排ガス中に含まれる有機溶剤
を回収する活性炭吸着法において、活性炭を充填した2
基あるいはそれ以上の吸着槽を並列的に設け、吸着と活
性炭再生のための脱着を交互に繰り返す固定床式溶剤回
収装置あるいは棚段塔を設け、塔頂より活性炭を連続的
に降下させて塔底より送り込まれる空気及び溶剤の混合
ガス(以下原ガスと称する)により、この活性炭を流動
させつつ溶剤の吸着を行わせる流動層式吸着装置などが
公知である。In the activated carbon adsorption method for recovering the organic solvent contained in the exhaust gas generated by various operations such as the manufacturing process of various plastic products and various operations such as the magnetic tape industry, the activated carbon was filled with 2
A bed or more adsorption tanks are installed in parallel, and a fixed-bed solvent recovery device or a tray column is installed in which adsorption and desorption for regeneration of activated carbon are alternately repeated, and the activated carbon is continuously lowered from the top of the tower. A fluidized bed type adsorbing device, etc., which adsorbs a solvent while flowing the activated carbon by a mixed gas of air and a solvent (hereinafter referred to as raw gas) fed from the bottom, is known.
これらの吸着槽は一般に吸着、脱着共、大気圧下で運転
され、また脱着には水蒸気が使用される。これらの従来
法のうち2層固定床式吸着装置を第2図及び第1表(従
来法)により説明する。第1表は従来法、本発明方法に
ついて吸着槽操作条件の一例を示したものである。These adsorption tanks are generally operated under atmospheric pressure for both adsorption and desorption, and steam is used for desorption. Of these conventional methods, the two-layer fixed bed adsorption device will be described with reference to FIG. 2 and Table 1 (conventional method). Table 1 shows an example of operating conditions of the adsorption tank for the conventional method and the method of the present invention.
第2図において原ガス1はブロワー2により吸着槽3−
1または3−2のいずれか一方に送り込まれ、原ガス中
の溶剤は固定床を形成する活性炭に吸着され、浄化され
た廃ガスは大気に放出される。例えば吸着槽3−1にお
いて吸着操作が行われるとすると、他方の吸着槽3−2
は吸着を終了し切換弁によって吸着から脱着に切換えら
れ、水蒸気Sが吹込まれて吸着された溶剤は脱着されて
水蒸気と共にガス状で排出される。この混合蒸気(脱着
蒸気)は凝縮器5に導かれて水冷却によって全量凝縮さ
れる。この際水と回収溶剤が相互に不溶の場合には、デ
カンター9において比重差により溶剤層と水層の2層に
分かれ、水は排出され、溶剤は回収される。また両者が
相互に一部または全部溶け合う場合には適宜蒸留塔(図
示せず)へ送られ水と溶剤の分離が行われる。この際凝
縮器5の凝縮側はベント管10によって大気に通じてお
り、従って脱着は大気圧下で行われる。この方式では吸
着工程より脱着工程に切換えられた初期は活性炭温度は
吸着温度(一般に30℃前後)にあり、吸込まれた水蒸気
は凝縮しつつ炭層温度を上昇させ100℃に至った後炭層
中に滞留している原ガスを排出させ、続いて脱着蒸気が
吸着槽より排出され、脱着は100℃において続行され
る。脱着工程終了後、その吸着槽は吸着工程に切換えら
れ、吸着槽には原ガスが吹込まれる。この際脱着後の炭
層温度は100℃にあり、活性炭中の水分(凝縮水蒸気)
が原ガス中に蒸発することにより、その蒸発熱で炭層の
温度は徐々に低下し、原ガス中の溶剤の吸着が進行す
る。In FIG. 2, the raw gas 1 is absorbed by the blower 2 in the adsorption tank 3-
The solvent in the raw gas is adsorbed by the activated carbon forming the fixed bed, and the purified waste gas is released to the atmosphere. For example, if an adsorption operation is performed in the adsorption tank 3-1, the other adsorption tank 3-2
Ends adsorption and is switched from adsorption to desorption by a switching valve. The water vapor S is blown in and the adsorbed solvent is desorbed and discharged in a gaseous state together with the water vapor. This mixed vapor (desorption vapor) is guided to the condenser 5 and is wholly condensed by water cooling. At this time, when the water and the recovered solvent are mutually insoluble, the decanter 9 separates into two layers, a solvent layer and an aqueous layer, due to the difference in specific gravity, and the water is discharged and the solvent is recovered. When the two are partially or wholly soluble in each other, they are appropriately sent to a distillation column (not shown) to separate water and solvent. At this time, the condenser side of the condenser 5 communicates with the atmosphere through the vent pipe 10, so that desorption is performed under atmospheric pressure. In this system, the activated carbon temperature is at the adsorption temperature (generally around 30 ° C) at the initial stage when the adsorption process is switched to the desorption process, and the absorbed water vapor condenses and raises the coalbed temperature to reach 100 ° C. The stagnant raw gas is discharged, then the desorption vapor is discharged from the adsorption tank, and the desorption is continued at 100 ° C. After the desorption process is completed, the adsorption tank is switched to the adsorption process, and the raw gas is blown into the adsorption tank. At this time, the temperature of the coal bed after desorption is 100 ° C, and the water in the activated carbon (condensed steam)
When the gas is evaporated into the raw gas, the temperature of the coal bed is gradually lowered by the heat of evaporation, and the adsorption of the solvent in the raw gas proceeds.
ところで、近年磁気テープ製造あるいは合成樹脂加工工
業においてケトン系溶剤としてメチルエチルケトン、メ
チルイソブチルケトン、シクロヘキサノン等が多量に使
用されるようになった。これらケトン系溶剤は吸脱着の
際、活性炭上で酸化、分解、重合等の反応を起こし易
く、回収製品の純度、活性炭の吸着能力保持期間あるい
は炭層着火に対する安全上の問題が生じている。例え
ば、メチルエチルケトンは活性炭の触媒作用により酸化
を受け、ジアセチル酢酸等を生成し、回収溶剤が黄色に
着色して製品純度を損ねる。またシクロヘキサノンも酸
化を受けてシクロヘキサンジオン、アジピン酸等を生成
する。これらの酸化物は沸点が高く、脱着工程において
容易に脱着されず、活性炭細孔内に蓄積し、徐々に活性
炭の吸着性能を低下させる。さらにこれらケトン系溶剤
は酸化により過酸化物を生成し、屡々炭層の着火を惹き
起こす原因となっている。この酸化反応は吸着工程が終
了し、脱着工程に入った初期、炭層には原ガス中の空気
が存在し、ここに水蒸気が吹込まれ、水蒸気の凝縮によ
り炭層が高温に加熱されることから、活性炭中に吸着さ
れている溶剤が酸素の存在下、活性炭の触媒作用によっ
て激しく起こる。また脱着が終了し、吸着に入った初
期、炭層がまだ高温であり、ここに原ガスが送入されれ
ば、活性炭中に残留している溶剤と共に、脱着初期と同
様、高温、酸素の存在下、活性炭の触媒作用で溶剤の酸
化が激しく起こることが考えられる。By the way, in recent years, a large amount of methyl ethyl ketone, methyl isobutyl ketone, cyclohexanone or the like has been used as a ketone solvent in the magnetic tape manufacturing or the synthetic resin processing industry. During adsorption and desorption, these ketone solvents are apt to undergo reactions such as oxidation, decomposition and polymerization on the activated carbon, which poses safety problems with respect to the purity of the recovered product, the activated carbon adsorption capacity retention period and coal bed ignition. For example, methyl ethyl ketone is oxidized by the catalytic action of activated carbon to produce diacetylacetic acid and the like, and the recovered solvent is colored yellow to impair the product purity. Cyclohexanone is also oxidized to produce cyclohexanedione, adipic acid and the like. These oxides have high boiling points, are not easily desorbed in the desorption process, accumulate in the activated carbon pores, and gradually reduce the adsorption performance of the activated carbon. Furthermore, these ketone solvents generate peroxides by oxidation, which often causes ignition of coal layers. In this oxidation reaction, when the adsorption step is completed and the desorption step is started, air in the raw gas is present in the coal bed, and steam is blown into the coal bed, and the coal bed is heated to a high temperature by condensation of the steam. The solvent adsorbed in the activated carbon is violently generated by the catalytic action of the activated carbon in the presence of oxygen. In addition, when desorption is completed and adsorption starts, the coal layer is still at a high temperature, and if raw gas is fed into this, along with the solvent remaining in the activated carbon, high temperature and the presence of oxygen will be present as in the desorption initial stage. Below, it is considered that the oxidation of the solvent occurs violently due to the catalytic action of activated carbon.
したがってこれらの溶剤の反応抑止が強く要望されてい
る。Therefore, suppression of reaction of these solvents is strongly demanded.
本発明は上記課題を解決するためになされたもので、そ
の目的とするところは脱着、さらには吸着の際活性炭に
吸着された溶剤の分解、酸化、重合などの反応を抑止
し、活性炭の寿命を長くしようとすることにある。The present invention has been made to solve the above problems, and its purpose is to desorb, further suppress the reaction such as decomposition of the solvent adsorbed on the activated carbon during adsorption, oxidation, polymerization, etc., the life of the activated carbon Is trying to lengthen.
本発明者らは上記目的を達成するため、活性炭上におけ
る溶剤の酸化等の反応速度は温度によって変り、低温に
なるにつれてこれらの反応速度が大きく低下することを
見出し、水蒸気脱着の初期において低圧低温の水蒸気を
用いて炭層内の空気を追出し、しかる後所定の温度の水
蒸気を用いて脱着を行い、脱着終了後は、炭層内に残留
充満する水蒸気を凝縮器によって水冷凝縮させることに
より吸着槽内を減圧し、圧力の低下によって水の沸点が
下がるため、水蒸気脱着後の活性炭に含まれる水分の蒸
発が起こり、その際水の蒸発熱によって炭層温度を低下
させる。炭層の温度が所定の温度迄低下した後、吸着工
程に移り、炭層に原ガスを通過させる。In order to achieve the above-mentioned object, the present inventors have found that the reaction rate such as the oxidation of the solvent on the activated carbon changes depending on the temperature, and that the reaction rate greatly decreases as the temperature decreases, and low pressure low temperature at the initial stage of steam desorption. The air in the coal seam is expelled using the steam of, and then desorption is performed using the steam of a predetermined temperature, and after the desorption is completed, the steam remaining in the coal seam is condensed by water-cooling with a condenser in the adsorption tank. Since the boiling point of water is lowered by reducing the pressure, the water contained in the activated carbon after steam desorption is evaporated, and at this time, the coal layer temperature is lowered by the heat of evaporation of water. After the temperature of the coal seam has dropped to a predetermined temperature, the process proceeds to the adsorption step, and the raw gas is passed through the coal seam.
この脱着−吸着方式によって活性炭とこれに含まれる溶
剤が、高温において空気と接触することなく、水蒸気脱
着が行われる。By this desorption-adsorption method, steam desorption is carried out without the activated carbon and the solvent contained therein contacting with air at high temperature.
以下に本発明方法を第1図及び第1表(本発明方法)に
基づき説明する。The method of the present invention will be described below with reference to FIG. 1 and Table 1 (method of the present invention).
第1図は本発明の一実施態様を示すフロー図である。第
1図において吸着槽3−1は吸着工程にあり、また吸着
槽3−2は脱着工程にあるとする。ここで吸着槽3−2
は吸着工程に切換えた初期においては吸着槽内は原ガス
で充満しており、ほぼ大気圧下にある。このような状態
にある吸着槽3−2内のガスを、脱着工程開始と共に真
空ポンプ6により凝縮器5のベント管10を通して吸引
し、吸着槽3−2を減圧し所定の圧力とする。一方吸引
したガスは原ガスのブロワー2の出口の導管に接続す
る。FIG. 1 is a flow chart showing an embodiment of the present invention. In FIG. 1, the adsorption tank 3-1 is in the adsorption step, and the adsorption tank 3-2 is in the desorption step. Here, adsorption tank 3-2
In the initial stage after switching to the adsorption step, the adsorption tank was filled with the raw gas, and was at about atmospheric pressure. The gas in the adsorption tank 3-2 in such a state is sucked through the vent pipe 10 of the condenser 5 by the vacuum pump 6 when the desorption process is started, and the adsorption tank 3-2 is depressurized to a predetermined pressure. On the other hand, the sucked gas is connected to the conduit at the outlet of the raw gas blower 2.
その後水蒸気Sを減圧弁PCV−1により吸着槽3−2と
ほぼ等しい圧力に減圧し、さらにこの水蒸気が減圧され
た圧力における過熱水蒸気温度状態となるので、これを
その圧力における飽和水蒸気温度まで冷却するため水W
を温度調節弁TCVを通して水蒸気中に送入し、水の蒸発
により飽和水蒸気温度に至った水蒸気を吸着槽3−2に
送入し炭層4−2の加熱を行う。炭層4−2の温度は送
入された水蒸気の凝縮により、吸着工程における温度
(一般に30℃前後)から、減圧加熱温度、すなわち水蒸
気の所定圧力における飽和温度まで上昇する。この炭層
温度上昇は炭層上部より水蒸気温度に到達し、それと共
にその部分の水蒸気の凝縮は止み、その部分の炭層内に
滞留する空気は水蒸気の通過により下方へ押出され、こ
れが徐々に炭層下部に向って進行し炭層全体が水蒸気温
度と等しい温度に至った時点において、炭層内の空気は
ほぼ完全に排出される。After that, the steam S is depressurized to a pressure almost equal to that of the adsorption tank 3-2 by the depressurization valve PCV-1, and the steam becomes a superheated steam temperature state at the depressurized pressure. Therefore, the steam S is cooled to the saturated steam temperature at the pressure. Water W to do
Is sent into the steam through the temperature control valve TCV, and the steam having reached the saturated steam temperature by the evaporation of water is sent to the adsorption tank 3-2 to heat the coal bed 4-2. The temperature of the coal bed 4-2 rises from the temperature in the adsorption step (generally around 30 ° C.) to the reduced pressure heating temperature, that is, the saturation temperature at a predetermined pressure of the steam, due to the condensation of the introduced steam. This rise in the temperature of the coal seam reaches the steam temperature from the upper part of the coal seam, at the same time the condensation of steam in that part stops, and the air staying in the coal seam in that part is extruded downward due to the passage of steam, and this gradually becomes to the lower part of the coal seam. The air in the coal seam is almost completely discharged at the time when the temperature of the entire coal seam reaches the temperature equal to the steam temperature.
従来法においては炭層全体が脱着温度(100℃)に至る
時間は一般の装置において、水蒸気送入開始より、0.5
〜1時間であり、この時間帯に有機溶剤が活性炭及び空
気の存在下、高温に曝されることになり、溶剤が最も激
しく酸化反応を起こすことになる。酸化反応速度が温度
の低下に従って減少することは自明のことであるが、炭
層内の空気を脱着初期において排出するに当り、100℃
の水蒸気を用いて炭層を100℃迄加熱して空気の除去を
行う従来法に比較して、低圧力低温度の水蒸気を用いて
行うことは溶剤の酸化を抑制する上で大きい効果が得ら
れる。In the conventional method, the time required for the entire coal bed to reach the desorption temperature (100 ° C) was 0.5
It is ~ 1 hour, and the organic solvent is exposed to high temperature in the presence of activated carbon and air during this time, and the solvent causes the most vigorous oxidation reaction. It is self-evident that the oxidation reaction rate decreases as the temperature decreases, but when the air in the coal seam is exhausted at the initial stage of desorption, 100 ° C
Compared with the conventional method of heating the coal bed to 100 ° C to remove the air by using the above steam, the use of steam at low pressure and low temperature has a great effect on suppressing the oxidation of the solvent. .
炭層全体が所定減圧下における飽和水蒸気温度に到達
後、真空ポンプ6を停止し、脱着弁V−Bを閉とし、次
いで水蒸気Sを圧力ほぼ1atm、温度約100℃において吸
着槽3−2に送入することにより、炭層4−2はさらに
水蒸気の凝縮が起こり、約100℃に到達する。このよう
にして炭層が約100℃に到達した後、脱着弁V−Bを開
とし続いて約100℃の水蒸気を所定時間送入することに
より活性炭に吸着された溶剤の脱着が行われる。脱着を
低圧低温水蒸気によって行わず100℃水蒸気で行う理由
は、低温になるにつれて脱着に要する水蒸気量が増大す
ることであり、炭層より空気を排除した後では高温にお
いても溶剤の酸化が起らないことによる。After the entire coal bed reached the saturated steam temperature under a predetermined reduced pressure, the vacuum pump 6 was stopped, the desorption valve V-B was closed, and then steam S was sent to the adsorption tank 3-2 at a pressure of about 1 atm and a temperature of about 100 ° C. By entering the water, further condensation of steam occurs in the coal seam 4-2 and reaches about 100 ° C. After the coal layer reaches about 100 ° C. in this way, the desorption valve V-B is opened, and then steam at about 100 ° C. is fed for a predetermined time to desorb the solvent adsorbed on the activated carbon. The reason why desorption is not performed with low-pressure low-temperature steam at 100 ° C steam is that the amount of steam required for desorption increases as the temperature decreases, and after air is removed from the coal bed, solvent oxidation does not occur even at high temperatures. It depends.
脱着工程を終了し水蒸気の吸着槽3−2への送入を停止
後、吸着工程に入り原ガス1を吸着槽3−2に送入する
前に炭層4−2を脱着温度より所定の低温度迄冷却する
ために、凝縮器ベント管10のSVを全開とする。吸着槽3
−2及び凝縮器5は水蒸気によって充満されているが、
ベント管10を閉じることにより水蒸気が冷却水Wを通す
凝縮器5において水冷却凝縮されるにつれて吸着槽3−
2内の圧力は低下する。圧力の低下に伴い脱着温度にあ
る炭層4−2に含まれる水分(脱着初期における凝縮
水)は蒸発し、その蒸発熱(脱着熱:水の蒸発潜熱の約
1.3倍)により炭層の温度は降下する。この減圧冷却に
より炭層4−2が所定の温度に到達後、脱着工程は終了
し、開閉弁SV及び圧力調節弁PCV−2を開き吸着槽3−
2を大気圧に戻し、吸着工程に切換えられ原ガス1を送
入する。同時に吸着槽3−1は脱着工程に切換えられ、
減圧−減圧加熱−脱着−減圧冷却が行われる。After finishing the desorption process and stopping the feeding of water vapor to the adsorption tank 3-2, the coal bed 4-2 is cooled to a predetermined temperature lower than the desorption temperature before entering the adsorption process and feeding the raw gas 1 to the adsorption tank 3-2. The SV of the condenser vent pipe 10 is fully opened for cooling to the temperature. Adsorption tank 3
-2 and the condenser 5 are filled with steam,
By closing the vent pipe 10, as the water vapor passes through the cooling water W and is condensed by water cooling in the condenser 5, the adsorption tank 3-
The pressure in 2 drops. As the pressure decreases, the water (condensed water in the initial stage of desorption) contained in the coal seam 4-2 at the desorption temperature evaporates, and its heat of vaporization (desorption heat: about the latent heat of vaporization of water)
1.3 times), the temperature of the coal seam drops. After the coal bed 4-2 has reached a predetermined temperature by this reduced pressure cooling, the desorption process is completed, and the on-off valve SV and the pressure control valve PCV-2 are opened to open the adsorption tank 3-.
2 is returned to atmospheric pressure, the adsorption process is switched to, and the raw gas 1 is fed. At the same time, the adsorption tank 3-1 is switched to the desorption process,
Decompression-decompression heating-desorption-decompression cooling are performed.
この脱着後の減圧冷却は吸着槽付属の切換弁に多少の洩
れがあり減圧冷却時に空気の流入があり、減圧を阻害す
ることがある場合には開閉弁SVは使用せず、真空ポンプ
6を駆動し圧力調節弁PCV−2の設定圧力を炭層の到達
温度に対応する圧力に調節し、流入空気を排出しつつ所
定の減圧圧力を保持することも本発明に含まれる。なお
この圧力は冷却水Wの水温にも依存すことが明らかであ
る。In this depressurized cooling after desorption, if there is some leakage in the switching valve attached to the adsorption tank and there is air inflow during depressurized cooling, which may impede depressurization, the on-off valve SV is not used and the vacuum pump 6 is not used. The present invention also includes adjusting the set pressure of the driven pressure control valve PCV-2 to a pressure corresponding to the ultimate temperature of the coal seam, and maintaining a predetermined depressurization pressure while discharging the inflowing air. It is clear that this pressure also depends on the water temperature of the cooling water W.
この減圧冷却により、脱着後炭層に残留する溶剤が、高
温で空気と接触することなく冷却されるため残留溶剤の
酸化が防止されることになる。さらに吸着初期の新たな
吸着溶剤の酸化も防止される。By this reduced-pressure cooling, the solvent remaining in the coal bed after desorption is cooled at a high temperature without contacting with air, so that oxidation of the residual solvent is prevented. Furthermore, the oxidation of new adsorption solvent at the initial stage of adsorption is also prevented.
さらに溶剤の加熱による重合を抑制するために脱着を減
圧低温水蒸気を用いて行う場合があるが、その場合にお
いても溶剤の酸化を防止するために、炭層の脱着前の減
圧加熱(炭層よりの空気排除)を脱着におけるよりも、
さらに低圧力低温度水蒸気を使用して行い、また脱着後
の減圧冷却を脱着におけるよりも低圧力で行うことにつ
いてもこの発明に含まれる。In addition, desorption may be performed using reduced pressure low-temperature steam in order to suppress polymerization due to heating of the solvent, but in that case as well, in order to prevent oxidation of the solvent, heating under reduced pressure before desorption of the coal bed (air from the coal bed Exclusion) than in desorption
Further, it is included in the present invention that it is performed by using low pressure and low temperature steam, and that the reduced pressure cooling after desorption is performed at a lower pressure than that in desorption.
〔実施例〕 乾燥機より発生するシクロヘキサノン及びトルエンを含
むガス中から活性炭を充填した吸着槽2基を用い、1つ
は従来法の吸着と大気圧、100℃の水蒸気脱着による活
性炭再生を繰返すサイクルによる方式、他は本発明方法
による吸着と減圧水蒸気加熱、100℃水蒸気脱着、減圧
冷却による活性炭再生を繰返すサイクルによる方式によ
って同じ仕様条件下において溶剤回収を行った場合の運
転条件と活性炭寿命(吸着槽排ガス溶剤濃度が規定値を
越えるまでの運転時間)について第2表に比較して示
す。 [Example] Using two adsorption tanks filled with activated carbon from a gas containing cyclohexanone and toluene generated from a dryer, one is a cycle in which adsorption by the conventional method and regeneration of activated carbon by steam desorption at 100 ° C. at atmospheric pressure are repeated. By the method according to the present invention and the method by the cycle of repeating adsorption by the method of the present invention and steam heating under reduced pressure, steam desorption at 100 ° C., and regeneration of activated carbon by cooling under reduced pressure under the same specification conditions. Table 2 compares the operating time until the concentration of exhaust gas in the tank exceeds the specified value).
運転条件 溶剤(シクロヘキサノン、トルエン)含有ガス流量10,0
00Nm3/H ガス中の溶剤濃度 2360volppm 溶剤回収量 トルエン50Kg/H シクロヘキサノン50Kg/H 吸着槽排ガス溶剤濃度規定量 〈100volppm 吸着槽(円筒賢型)2基 内径3.1mφ高さ3.0m 活性炭3,300Kg/基 切換時間 吸着3時間、脱着3時間 使用水蒸気 2Kg/cm2G 使用冷却水 30℃ なお吸着槽排ガス溶剤濃度が100volppmになるまでの時
間を示したのが第3図である。Operating conditions Gas flow rate containing solvent (cyclohexanone, toluene) 10,0
00Nm 3 / H Solvent concentration in gas 2360volppm Solvent recovery amount Toluene 50Kg / H Cyclohexanone 50Kg / H Adsorption tank exhaust gas solvent concentration Specified amount <100volppm Adsorption tank (cylinder wise type) 2 units Inner diameter 3.1m φ Height 3.0m Activated carbon 3,300Kg / Substrate switching time Adsorption 3 hours, desorption 3 hours Steam used 2Kg / cm 2 G Cooling water 30 ℃ Note that FIG. 3 shows the time until the concentration of the exhaust gas solvent in the adsorption tank reaches 100 volppm.
従来法では着脱初期、空気の存在下高温にさらされた溶
剤が酸化され、また吸着初期に送入された原ガスが加熱
されるので活性炭中に酸化物が生成し蓄積されるので、
活性炭の寿命が短い。これに対し本発明方法では吸着槽
の減圧を行い低温水蒸気を送入して空気を排出した後、
大気圧水蒸気によって脱着が行われため溶剤の酸化が抑
制される。また脱着後、減圧による水分の蒸発熱によっ
て炭層の冷却を行った後、吸着工程にて原ガスが送入さ
れるので酸化が抑制される。In the conventional method, the solvent exposed to high temperature in the presence of air is oxidized in the conventional method, and the raw gas fed in the initial stage of adsorption is heated, so that oxides are generated and accumulated in the activated carbon.
The life of activated carbon is short. On the other hand, in the method of the present invention, after decompressing the adsorption tank and feeding low temperature steam to discharge air,
Oxidation of the solvent is suppressed because desorption is performed by atmospheric pressure steam. After desorption, the coal layer is cooled by the heat of evaporation of water due to the reduced pressure, and the raw gas is fed in the adsorption step, so that the oxidation is suppressed.
これら酸化抑制の効果により、本発明方法における一定
の吸脱着条件下での吸着槽排ガス溶剤濃度が100volppm
を越えるまでの期間(活性炭寿命)は従来法の約3倍と
長い。これは活性炭交換費用が従来の1/3以下で済むこ
とになり、溶剤の回収コストを大幅に低下させるので経
済的効果は大きい。Due to the effect of these oxidation suppression, the adsorption tank exhaust gas solvent concentration under constant adsorption and desorption conditions in the method of the present invention is 100 volppm
It takes about 3 times longer than that of the conventional method. This means that the activated carbon replacement cost will be less than 1/3 of the conventional cost, and the recovery cost of the solvent will be greatly reduced, so the economic effect is great.
また酸化物の生成が抑制されることにより回収溶剤の収
率、品質の向上が達成される。Further, by suppressing the generation of oxides, the yield and quality of the recovered solvent can be improved.
第1図は本発明の減圧加熱、大気圧脱着、減圧冷却方式
のフロー図である。第2図は従来の大気圧加熱、大気圧
脱着方式のフロー図である。 第3図は溶剤回収運転期間と吸着槽排ガス溶剤濃度推移
関係図(実施例)である。 1……原ガス、2……ガスブロワー 3−1,3−2……吸着槽、4−1,4−2……活性炭層 5……凝縮器、6……真空ポンプ 7……中継槽、8……送液ポンプ 9……デカンター、10……ベント管 S……水蒸気、W……冷却水 PCV−1……水蒸気圧力調節弁 PCV−2……真空ポンプ圧力調節弁 TCV……水蒸気温度調節弁 SV……遮断弁 V−B……脱着弁FIG. 1 is a flow chart of the reduced pressure heating, atmospheric pressure desorption and reduced pressure cooling system of the present invention. FIG. 2 is a flow chart of a conventional atmospheric pressure heating and atmospheric pressure desorption method. FIG. 3 is a diagram showing the relationship between solvent recovery operation period and adsorption tank exhaust gas solvent concentration transition (Example). 1 ... Raw gas, 2 ... Gas blower 3-1, 3-2 ... Adsorption tank, 4-1, 4-2 ... Activated carbon layer 5 ... Condenser, 6 ... Vacuum pump 7 ... Relay tank , 8 ... Liquid feed pump 9 ... Decanter, 10 ... Vent pipe S ... Steam, W ... Cooling water PCV-1 ... Steam pressure control valve PCV-2 ... Vacuum pump pressure control valve TCV ... Steam Temperature control valve SV ... Shut-off valve V-B ... Desorption valve
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/44 53/81 B01J 20/34 B 7202−4G ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location B01D 53/44 53/81 B01J 20/34 B 7202-4G
Claims (1)
を吸着させ次いで活性炭に吸着された該ガスを脱着する
ため活性炭層に直接所定の水蒸気を吹込んで活性炭を再
生する方法において、前記水蒸気を吹込む以前に、吸着
槽内を減圧し、次いで前記水蒸気の温度以下の水蒸気を
吹込み、その減圧圧力の飽和温度における水蒸気によっ
て活性炭層の空気を置換した後、前記水蒸気を吹込んで
脱着を行い、前記水蒸気吹込みを停止した後、吸着槽内
を脱着時の圧力以下に減圧し、活性炭に含まれる水分の
蒸発熱により、活性炭層の温度を脱着温度から減圧圧力
における水蒸気飽和温度付近迄冷却した後、吸着工程に
移ることを特徴とする活性炭再生方法。1. A method for regenerating activated carbon by adsorbing a solvent gas using an adsorption tank filled with activated carbon and then injecting a predetermined vapor directly into the activated carbon layer to desorb the gas adsorbed on the activated carbon. Before blowing in, the pressure in the adsorption tank is reduced, then steam below the temperature of the steam is blown, the air in the activated carbon layer is replaced by steam at the saturation temperature of the reduced pressure, and then the steam is blown for desorption. After stopping the steam injection, the pressure inside the adsorption tank is reduced to the pressure at the time of desorption or less, and the temperature of the activated carbon layer is changed from the desorption temperature to near the steam saturation temperature at the depressurized pressure by the heat of vaporization of the water contained in the activated carbon. A method for regenerating activated carbon, characterized by moving to an adsorption step after cooling.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1214105A JPH0732861B2 (en) | 1989-08-22 | 1989-08-22 | Activated carbon regeneration method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1214105A JPH0732861B2 (en) | 1989-08-22 | 1989-08-22 | Activated carbon regeneration method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0377619A JPH0377619A (en) | 1991-04-03 |
| JPH0732861B2 true JPH0732861B2 (en) | 1995-04-12 |
Family
ID=16650317
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1214105A Expired - Fee Related JPH0732861B2 (en) | 1989-08-22 | 1989-08-22 | Activated carbon regeneration method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0732861B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108317646B (en) * | 2017-12-23 | 2024-01-02 | 天津沐歌医疗科技发展有限公司 | Air purification device based on air source heat pump |
| CN107970904B (en) * | 2018-01-26 | 2023-06-20 | 索红卫 | Activated carbon regeneration system and use method |
-
1989
- 1989-08-22 JP JP1214105A patent/JPH0732861B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0377619A (en) | 1991-04-03 |
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