JPH0796075B2 - Method for operating solvent gas recovery device using activated carbon - Google Patents
Method for operating solvent gas recovery device using activated carbonInfo
- Publication number
- JPH0796075B2 JPH0796075B2 JP20786988A JP20786988A JPH0796075B2 JP H0796075 B2 JPH0796075 B2 JP H0796075B2 JP 20786988 A JP20786988 A JP 20786988A JP 20786988 A JP20786988 A JP 20786988A JP H0796075 B2 JPH0796075 B2 JP H0796075B2
- Authority
- JP
- Japan
- Prior art keywords
- activated carbon
- dry cleaner
- solvent
- solvent gas
- tank
- 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 - Lifetime
Links
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims description 206
- 239000002904 solvent Substances 0.000 title claims description 44
- 238000011084 recovery Methods 0.000 title claims description 20
- 238000000034 method Methods 0.000 title claims description 16
- 238000001035 drying Methods 0.000 claims description 7
- 238000001179 sorption measurement Methods 0.000 description 14
- 230000001877 deodorizing effect Effects 0.000 description 13
- 238000003795 desorption Methods 0.000 description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 10
- 238000004332 deodorization Methods 0.000 description 5
- 238000010586 diagram Methods 0.000 description 5
- CYTYCFOTNPOANT-UHFFFAOYSA-N Perchloroethylene Chemical group ClC(Cl)=C(Cl)Cl CYTYCFOTNPOANT-UHFFFAOYSA-N 0.000 description 4
- 229950011008 tetrachloroethylene Drugs 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 230000005484 gravity Effects 0.000 description 3
- 239000003960 organic solvent Substances 0.000 description 3
- 230000005856 abnormality Effects 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 238000005238 degreasing Methods 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- 238000003915 air pollution Methods 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 239000003599 detergent Substances 0.000 description 1
- 238000005108 dry cleaning Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 238000005192 partition Methods 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Description
【発明の詳細な説明】 (産業上の利用分野) 本発明は、ドライクリーニング業界の溶剤ガス回収装
置、或いは有機溶剤を使用し、金属脱脂等の為に脱脂槽
を用いた金属洗浄後の溶剤ガス回収装置等の運転方法に
関する。DETAILED DESCRIPTION OF THE INVENTION (Industrial field of application) The present invention relates to a solvent gas recovery device in the dry cleaning industry, or an organic solvent, and a solvent after metal cleaning using a degreasing tank for degreasing metal or the like. The present invention relates to a method of operating a gas recovery device or the like.
(従来の技術) 活性炭による吸着回収技術は様々な方式で公知である
が、例えばドライクリーナと組合せるときの溶剤回収装
置を第3図及び第4図に基づき説明する。(Prior Art) The adsorption recovery technology using activated carbon is known in various ways. For example, a solvent recovery apparatus when combined with a dry cleaner will be described with reference to FIGS. 3 and 4.
パークロルエチレン、1.1.1−トリクロルエタン、フレ
オンR113等の有機溶剤を使用するドライクリーナは、一
般に次の工程の如く運転される。(図示せず) (1) 洗浄工程 ドライクリーナの回転ドラム内に衣料を入れ有機溶剤中
に洗剤を入れ洗浄する。A dry cleaner using an organic solvent such as perchlorethylene, 1.1.1-trichloroethane, Freon R113 or the like is generally operated in the following steps. (Not shown) (1) Washing step Put clothes in the rotary drum of the dry cleaner and put detergent in an organic solvent for washing.
(2) 排液及び脱液工程 洗浄した衣料を高速回転させ遠心脱水する。(2) Drainage and drainage process The washed clothes are spun at high speed to spin-dry.
(3) 乾燥工程 衣料に付いている溶剤に熱風を吹きつけ乾燥させる。こ
の際、衣料から蒸発した溶剤ガスは凝縮機で回収する。(3) Drying process Hot air is blown to the solvent on the clothing to dry it. At this time, the solvent gas evaporated from the clothing is collected by the condenser.
(4) 脱臭工程 乾燥後でも若干衣料に残留する溶剤分に対し、外気を導
入して衣料と接触させ蒸発させる。即ち、脱臭(脱気)
を行う。(4) Deodorizing step For the solvent content that remains in the clothing slightly even after drying, the outside air is introduced to contact with the clothing and evaporate. That is, deodorization (deaeration)
I do.
前記(4)項の脱臭工程において、蒸発溶剤は大気放出
されて溶剤ロスになるばかりか大気汚染に連なる為、こ
れを活性炭で吸着回収する。また、これらの他にドライ
クリーナを運転していると、ドライクリーナ内の温度変
化に伴い溶剤ガスが膨張する為、これを通気管を介して
ドライクリーナ外に排出する。In the deodorizing step of the above item (4), the evaporating solvent is released into the air to cause a solvent loss as well as air pollution. Therefore, this is adsorbed and recovered by activated carbon. Further, when the dry cleaner is operated in addition to these, the solvent gas expands with the temperature change in the dry cleaner, and this is discharged to the outside of the dry cleaner through the ventilation pipe.
脱臭及び内圧膨張による溶剤ガスの回収方法を第3図に
より説明する。A method of recovering the solvent gas by deodorizing and expanding the internal pressure will be described with reference to FIG.
同図において1は活性炭を示し、2は活性炭を内蔵する
タンク(活性炭槽)、7,8はタンクの出口と入口に付属
するダンパである。3はコンデンサで、通常水を通して
冷却する機能を持つ。4は水分分離器で、比重差で溶剤
と水とに分離する。これらの2,3,4で構成する部分が回
収装置の主構成部である。5はドライクリーナ本体、6
はドライクリーナ内のタンクを示している。In the figure, 1 is activated carbon, 2 is a tank containing activated carbon (activated carbon tank), and 7 and 8 are dampers attached to the outlet and inlet of the tank. 3 is a condenser, which usually has a function of cooling through water. A water separator 4 separates the solvent and water due to the difference in specific gravity. The part composed of these 2, 3 and 4 is the main constituent part of the recovery device. 5 is the main body of the dry cleaner, 6
Indicates the tank in the dry cleaner.
ドライクリーナ本体5の脱臭工程で排出した溶剤ガス
は、導管11を経て入口ダンパ8、活性炭1を経由し、出
口ダンパ7から大気へ放出する。この時、活性炭を通過
した溶剤ガスの溶剤分の殆どは活性炭に吸着され、活性
炭を出る時は50ppm以下になるのが普通である。活性炭
の吸着能力は活性炭量に比例する。ある負荷に対して吸
着出来なくなる回数(脱臭数)は予測可能である。活性
炭が吸着出来なくなると、脱着工程(再生とも言う。)
となり、活性炭槽タンク1の出入口ダンパ7,8を閉じて
9の弁を開して水蒸気を入れる。この熱によって活性炭
中の溶剤分は蒸発し、導管12を経てコンデンサ3に達す
る。コンデンサ3では、溶剤ガス及び水蒸気は冷却され
凝縮液化する。液化した溶剤と水は水分分離器4で溶剤
と水に分けられる。例えば、パークロルエチレンは比重
1.62、水は1であるから、パークロルエチレンは底部寄
りに溜まり、水は上部に浮く。溶剤は回収管10を経てド
ライクリーナ本体のタンク6に戻る。水は排水として系
外に排出される。The solvent gas discharged in the deodorizing step of the dry cleaner main body 5 is discharged to the atmosphere from the outlet damper 7 through the conduit 11, the inlet damper 8 and the activated carbon 1. At this time, most of the solvent component of the solvent gas that has passed through the activated carbon is adsorbed by the activated carbon, and when leaving the activated carbon, it is usually 50 ppm or less. The adsorption capacity of activated carbon is proportional to the amount of activated carbon. It is possible to predict the number of times (deodorization number) that adsorption cannot be performed for a certain load. When activated carbon cannot be adsorbed, the desorption process (also called regeneration)
Then, the inlet and outlet dampers 7 and 8 of the activated carbon tank 1 are closed, and the valve 9 is opened to add steam. Due to this heat, the solvent content in the activated carbon is evaporated and reaches the condenser 3 via the conduit 12. In the condenser 3, the solvent gas and water vapor are cooled and condensed and liquefied. The liquefied solvent and water are separated into a solvent and water by a water separator 4. For example, perchlorethylene has a specific gravity
1.62, the water is 1, so perchlorethylene collects near the bottom and the water floats at the top. The solvent returns to the tank 6 of the dry cleaner body through the recovery pipe 10. Water is discharged outside the system as waste water.
第4図は双胴式と呼ばれる活性炭タンク(活性炭槽)が
2つから構成されるもので、その働きは第3図に示した
ものと同じてあるが、一方の活性炭槽が吸着可能な状態
となっている時、他方は脱着を行う。従って、常に一方
は開状態となっている。即ち、の活性炭槽1aが吸着状
態の時は出入口ダンパ7a,8aは開となって、ドライクリ
ーナの脱臭時に溶剤ガスは入口ダンパ8a→活性炭1a→出
口ダンパ7aと流れ排気する。他方の活性炭槽では出入
口ダンパ7b,8bが閉じ、水蒸気を弁9bから吹き込み脱着
を行う。ドライクリーナとこれらの活性炭の動作をチャ
ート図で示したものが第5図である。Fig. 4 shows that the activated carbon tank (activated carbon tank) called the twin-body type is composed of two, and its function is the same as that shown in Fig. 3, but one activated carbon tank can be adsorbed. , The other will do desorption. Therefore, one side is always open. That is, when the activated carbon tank 1a is in the adsorption state, the inlet / outlet dampers 7a and 8a are opened, and when the dry cleaner is deodorized, the solvent gas flows from the inlet damper 8a → the activated carbon 1a → the outlet damper 7a and is exhausted. In the other activated carbon tank, the inlet and outlet dampers 7b and 8b are closed, and steam is blown from the valve 9b for desorption. FIG. 5 is a chart showing the operation of the dry cleaner and these activated carbons.
第3図に示すケースでは、活性炭はドライクリーナの一
工程の間に単一の活性炭槽で活性炭の吸着、脱着、活性
炭乾燥を行う。第4図に示すケースの場合は、1方の活
性炭はドライクリーナの全工程で吸着のみを行い、他方
の活性炭は脱着及び活性炭乾燥を行い次回の吸着に対応
させる準備を行うものである。即ち、第4図に示すケー
スにおいて、ドライクリーナの脱臭時、活性炭側は吸
着状態で、側は活性炭の乾燥状態になっている。In the case shown in FIG. 3, activated carbon is adsorbed, desorbed and dried in a single activated carbon tank during one step of the dry cleaner. In the case shown in FIG. 4, one of the activated carbons only adsorbs in all the steps of the dry cleaner, and the other activated carbon desorbs and dries the activated carbons to prepare for the next adsorption. That is, in the case shown in FIG. 4, when deodorizing the dry cleaner, the activated carbon side is in the adsorption state and the side is in the activated carbon dry state.
(発明が解決しようとする課題) 活性炭槽中の活性炭量の決定は活性炭の吸着能力と溶剤
負荷との見合いよって決められる。例えば、活性炭の吸
着能力はパークロルエチレンの場合、活性炭重量の20%
程度は可である。一方、活性炭の吸着能力は、活性炭槽
内の通過線速度が活性炭重量と風速によって活性炭の動
かない範囲(フローティングが起こらない範囲)、例え
ば0.4m/秒程度として決められる。即ち、風量が一定で
あれば活性炭槽の断面積は線速度で決定される。更に活
性炭と溶剤ガスとの見掛け接触時間は、約1秒程度が標
準値である。この様に風量によって断面積と高さが決定
され、活性炭量が決まる。(Problems to be Solved by the Invention) The amount of activated carbon in the activated carbon tank is determined by the balance between the adsorption capacity of activated carbon and the solvent load. For example, the adsorption capacity of activated carbon is 20% of the weight of activated carbon in the case of perchlorethylene.
The degree is acceptable. On the other hand, the adsorption capacity of activated carbon is determined as a range in which the linear velocity of passage in the activated carbon tank does not move (a range in which floating does not occur) due to the activated carbon weight and wind speed, for example, about 0.4 m / sec. That is, if the air volume is constant, the cross-sectional area of the activated carbon tank is determined by the linear velocity. Further, the apparent contact time between the activated carbon and the solvent gas is about 1 second as a standard value. In this way, the cross-sectional area and height are determined by the air volume, and the amount of activated carbon is determined.
ドライクリーナからの溶剤ガス排出はドライクリーナの
能力により異なるが、一般に衣料重量当り3.2%であ
る。従って、10kg/バッチのドライクリーナが脱臭時に
排出する溶剤ガス量は10×0.032=0.32kg程度となる。
一方、ドライクリーナの脱臭時の風量は0.5m3/kg衣料/
分程度が普通である。従って、10kg/バッチのドライク
リーナの場合、5m3/分の風量で脱臭することになる。Emission of solvent gas from the dry cleaner varies depending on the capacity of the dry cleaner, but is generally 3.2% based on the weight of the clothing. Therefore, the amount of solvent gas discharged by the 10 kg / batch dry cleaner during deodorization is approximately 10 × 0.032 = 0.32 kg.
On the other hand, the air volume when deodorizing the dry cleaner is 0.5 m 3 / kg clothing /
Minutes are normal. Therefore, in the case of a dry cleaner of 10 kg / batch, it will be deodorized with an air volume of 5 m 3 / min.
溶剤負荷に対して活性炭量を決めるとすると、10kg/バ
ッチのドライクリーナの場合、0.32kgの排出であり、吸
着能力は活性炭重量の20%であるから活性炭量は1.6kg
で良いことになる。しかし、風量による制限から活性炭
量を決めるとすると、Q=Avにより(Q=風量、A=断
面積、v=線速度) で、接触時間を1秒とすると層高0.4mとなり、容積は0.
208×0.4=0.083m3となる。活性炭の見掛比重は約0.4kg
/であるから、0.083m3×1000/m3×0.4kg/=33.2k
gの活性炭が必要となる。以上からドライクリーナの活
性炭吸着方式の活性炭量を決めるのは活性炭の通過風速
であり、この様に決めた装置では吸着負荷に余裕があり
すぎる。最大風量及び負荷が必要なのはドライクリーナ
の脱臭時であり、脱臭時の活性炭通路は単一の活性炭槽
であるのが従来の回収装置である。従って、第4図の双
胴式の1方の活性炭量は第3図の活性炭量と動じにな
る。即ち、第4図に示す装置で第3図に示す装置に対し
て2倍の活性炭が必要となる。When determining the amount of activated carbon for solvent load, 0.32 kg is discharged in the case of 10 kg / batch dry cleaner, and the adsorption capacity is 20% of the weight of activated carbon, so the amount of activated carbon is 1.6 kg.
Will be good. However, if the amount of activated carbon is determined from the limitation by the air volume, Q = Av (Q = air volume, A = cross-sectional area, v = linear velocity) Then, if the contact time is 1 second, the layer height becomes 0.4 m and the volume is 0.
It becomes 208 × 0.4 = 0.083m 3 . Apparent specific gravity of activated carbon is about 0.4 kg
Therefore, 0.083m 3 × 1000 / m 3 × 0.4kg / = 33.2k
g of activated carbon is required. From the above, it is the passing wind velocity of the activated carbon that determines the amount of activated carbon in the activated carbon adsorption method of the dry cleaner, and the device thus determined has too much adsorption load. The maximum air volume and load are required during deodorization of the dry cleaner, and the conventional recovery device has a single activated carbon tank as the activated carbon passage during deodorization. Therefore, the amount of activated carbon in one of the twin-body type shown in FIG. 4 is in sync with the amount of activated carbon in FIG. That is, the apparatus shown in FIG. 4 requires twice as much activated carbon as the apparatus shown in FIG.
第3図に示す方式は活性炭槽が一つである為、脱着中に
は活性炭出入口とダンパが閉じる。この為ドライクリー
ナと大気とが閉状態となり、ドライクリーナの温度変化
に伴う体積膨張分が活性炭を通過出来ない為、ドライク
リーナの排水口などから装置外に排出し、室内環境を悪
くしたり、或いはドライクリーナの内圧が高くなること
で装置に異常を起こしたりする。一方、第4図に示す方
式では脱着中、一方の活性炭は常に大気に開放されてい
る為、体積膨張分は吸収出来る。なお、この体積膨張分
はガス濃度及び風量としては脱臭時の1/10程度である。Since the system shown in FIG. 3 has only one activated carbon tank, the activated carbon inlet and outlet and the damper are closed during desorption. For this reason, the dry cleaner and the atmosphere are closed, and the volume expansion due to the temperature change of the dry cleaner cannot pass through the activated carbon, so it is discharged to the outside of the device from the drain of the dry cleaner, etc. Alternatively, the internal pressure of the dry cleaner becomes high, which causes an abnormality in the device. On the other hand, in the system shown in FIG. 4, during desorption, one activated carbon is always open to the atmosphere, so that the volume expansion can be absorbed. The volume expansion amount is about 1/10 of the gas concentration and the air volume when deodorizing.
以上示した如く単胴式の活性炭量は双胴式の1/2で済む
が、内圧膨張分を吸収出来ないという欠点がある。一方
の双胴式は単胴式に比し活性炭量が2倍必要となる。As shown above, the amount of activated carbon in the single-cylinder type is half that in the double-cylinder type, but it has the drawback that it cannot absorb the internal pressure expansion. On the other hand, the twin cylinder type requires twice as much activated carbon as the single cylinder type.
本発明はこれらの欠点を同時に解決することを目的とし
てなされたものであり、使用活性炭量を単胴式と同量と
し、しかも常時一方の活性炭槽が開状態にある双胴式の
利点を生かす溶剤ガスの回収装置運転方法を提供するこ
とにある。The present invention has been made for the purpose of solving these drawbacks at the same time, and the amount of activated carbon used is the same as that of the single-cylinder type, and at the same time, one of the activated carbon tanks is always open, and the advantage of the double-drum type is utilized. It is to provide a method of operating a solvent gas recovery device.
(課題を解決するための手段及び作用) このため本発明は、活性炭を2槽に分割し、1槽の活性
炭が吸着状態にあるとき、他槽の活性炭の脱着並びに活
性炭乾燥を行う溶剤ガスの回収装置において、溶剤ガス
を発生させる機器から送られてくる溶剤ガスに対し両槽
の活性炭を共に吸着状態におくことを特徴とする活性炭
による溶剤ガスの回収装置運転方法を採用し、これを上
記課題の解決手段とするものである。(Means and Actions for Solving the Problem) Therefore, the present invention divides the activated carbon into two tanks, and when the activated carbon in one tank is in an adsorbed state, desorption of the activated carbon in another tank and drying of the activated carbon are performed. In the recovery device, the method for operating the recovery device of the solvent gas by the activated carbon is adopted, in which the activated carbon in both tanks is placed in an adsorbed state with respect to the solvent gas sent from the device that generates the solvent gas. This is a means for solving the problem.
これをドライクリーナにおける溶剤ガスの回収装置に採
用する場合につき説明する。A case where this is adopted in a solvent gas recovery device in a dry cleaner will be described.
(1) 活性炭槽を双胴式として構成し、ドライクリー
ナの排気風量を最大とする脱臭工程においては、2つの
活性炭槽で同時に吸着させる。(1) The activated carbon tank is configured as a twin-body type, and in the deodorizing process in which the exhaust air volume of the dry cleaner is maximized, the two activated carbon tanks are simultaneously adsorbed.
(2) ドライクリーナの脱臭工程以外の工程において
は、一方の活性炭槽は同じく吸着工程とし、他方の活性
炭槽は活性炭の脱臭及び活性炭乾燥工程として運転す
る。(2) In steps other than the deodorizing step of the dry cleaner, one of the activated carbon tanks is similarly operated as an adsorption step, and the other activated carbon tank is operated as a deodorizing step of activated carbon and an activated carbon drying step.
(3) 従って、最大風量に対しては2つの活性炭槽で
対応させる為、双胴式であっても単胴式と同量の活性炭
量で済み、従来の活性炭量の1/2のコンパクトな装置と
なる。(3) Therefore, since the maximum air volume is handled by two activated carbon tanks, the twin cylinder type requires the same amount of activated carbon as the single-cylinder type, which is half the conventional activated carbon volume. It becomes a device.
(実施例) 以下、本発明をドライクリーナに適用した場合の代表的
な実施例を図に基づいて説明する。第1図は本発明方法
を実施するためのドライクリーナに組込まれる溶剤回収
装置の概略構成を示し、同図における構成部品は第4図
に示した従来の双胴式溶剤回収装置と基本的に同じであ
る。従って、第4図に示す装置であっても本発明を実施
することは可能である。第1図と第4図の違いは、前者
が活性炭槽の2槽を一体化した例であり、後者が活性炭
槽を2槽に分割している例である点で異なるのみで、性
能的には何れの構成でも良い。ただ、本発明の場合に
は、ドライクリーナの脱臭工程では2個の活性炭槽2a,2
bに通じる出入口ダンパ7a,7b,8a,8bの全てを開くように
制御している。従って、ドライクリーナの脱臭工程とな
ると溶剤ガスは、導管11aを経て活性炭槽に流れるが、
2個の活性炭槽2a,2bの出入口ダンパ7a,7b,8a,8bは全て
開いているので、双方の活性炭1a,1bを通過し、ほぼ同
量の溶剤が双方の活性炭に吸着され、低濃度になった溶
剤ガスは排気管13を経由して屋外に排出される。(Example) Hereinafter, a typical example when the present invention is applied to a dry cleaner will be described with reference to the drawings. FIG. 1 shows a schematic structure of a solvent recovery device incorporated in a dry cleaner for carrying out the method of the present invention. The components in FIG. 1 are basically the same as those of the conventional twin barrel type solvent recovery device shown in FIG. Is the same. Therefore, the present invention can be implemented even with the device shown in FIG. The difference between FIG. 1 and FIG. 4 is that the former is an example in which two activated carbon tanks are integrated, and the latter is an example in which the activated carbon tank is divided into two tanks. May have any configuration. However, in the case of the present invention, two activated carbon tanks 2a, 2 are used in the deodorizing process of the dry cleaner.
All of the entrance / exit dampers 7a, 7b, 8a, 8b leading to b are controlled to open. Therefore, in the deodorizing step of the dry cleaner, the solvent gas flows to the activated carbon tank through the conduit 11a,
Since the inlet / outlet dampers 7a, 7b, 8a, 8b of the two activated carbon tanks 2a, 2b are all open, almost the same amount of solvent is adsorbed by both activated carbons and low concentration The generated solvent gas is discharged to the outside via the exhaust pipe 13.
ドライクリーナの全工程が終了し、次回の洗浄工程に入
ると、一方の活性炭槽2aは脱着工程に入る。従って、同
活性炭槽2aの出入口ダンパ7a,8aは閉となり、弁9aから
水蒸気を投入し、熱により活性炭1aに吸着された溶剤は
蒸発して逆止弁15a(自動弁でも可)を経由し、導管12a
を経てコンデンサに送られる。15bも逆止弁(自動弁で
も可)であり、活性炭糟2a側の脱着蒸気が他方の活性炭
糟2b側に流れ込まない様にしている。このとき、他方の
活性炭糟2bは、出入口ダンパ7b,8bが開いた状態のまま
にある為、ドライクリーナ側の温度変化により内部ガス
の体積膨張による内圧の上昇があっても、導管11aを経
由して入口ダンパ8b→活性炭1b→出口ダンパ7bを通って
排気管13から屋外に排気される。従って、大気開放状態
が常にどちらか一方に存在する為、装置への異常が防げ
る。When all the steps of the dry cleaner are completed and the next cleaning step is started, one activated carbon tank 2a enters the desorption step. Therefore, the inlet / outlet dampers 7a, 8a of the activated carbon tank 2a are closed, steam is introduced from the valve 9a, and the solvent adsorbed on the activated carbon 1a by heat evaporates and passes through the check valve 15a (which may be an automatic valve). , Conduit 12a
Sent to the condenser via. 15b is also a check valve (it may be an automatic valve) so that the desorbed vapor on the side of the activated carbon container 2a does not flow into the other activated carbon container 2b side. At this time, since the inlet / outlet dampers 7b, 8b of the other activated carbon tank 2b remain open, even if the internal pressure rises due to the volume expansion of the internal gas due to the temperature change on the dry cleaner side, it passes through the conduit 11a. Then, it is exhausted to the outside through the exhaust pipe 13 through the inlet damper 8b → the activated carbon 1b → the outlet damper 7b. Therefore, the open state to the atmosphere is always present in either one of the sides, so that an abnormality in the device can be prevented.
以上の操作を第2図にフローチャートで示している。The above operation is shown in the flow chart of FIG.
なお、両活性炭糟2aと2bの切り替えを、本実施例ではド
ライクリーナの一工程毎に行う場合について説明してい
るが、活性炭量と負荷(ドライクリーナ側の能力)によ
って、その切替える時期を変更することは可能であり、
ランニングコスト上も有効である。また、本実施例の説
明において活性炭の乾燥工程については説明を省略した
が、同工程は活性炭の脱着後に外気により活性炭中の水
分を排出乾燥させ、活性炭の吸着能力を復元する動作で
ある。更に本説明では、具体的な構造・方法は共に公知
の技術を採用すれば足りるものであるので、それらにつ
いての説明は省略した。また、第1図に示す装置では仕
切りを隔てて存在する活性炭同志が、一方の活性炭の脱
着時の熱伝導により他方の近接活性炭に熱影響を与える
ことが予想されるが、活性炭の間接加熱脱着では脱着が
困難であることは良く知られており、実用的に問題はな
い。In the present embodiment, switching between the two activated carbon tanks 2a and 2b is described for each step of the dry cleaner. However, the switching timing is changed depending on the amount of activated carbon and the load (capacity on the dry cleaner side). It is possible to
It is also effective in running cost. Although the description of the activated carbon drying step is omitted in the description of the present embodiment, the same step is an operation of recovering the adsorption capacity of the activated carbon by exhausting and drying the moisture in the activated carbon by the outside air after desorption of the activated carbon. Further, in the present description, it is sufficient to adopt a known technique for the specific structure and method, and therefore the description thereof is omitted. In addition, in the device shown in Fig. 1, it is expected that the activated carbons that are separated by partitions will have a thermal effect on the adjacent activated carbons due to heat conduction during desorption of one activated carbon. It is well known that it is difficult to put on and take off, so there is no practical problem.
(発明の効果) 以上、詳細に説明した如く本発明によると次に挙げる優
れた効果を奏する。(Effects of the Invention) As described in detail above, according to the present invention, the following excellent effects are obtained.
(1) 活性炭量が従来の双胴式装置に比し1/2の量で
構成出来る為、イニシャルコストを低減させ得る。(1) The initial cost can be reduced because the amount of activated carbon can be configured to be half that of the conventional twin-body type device.
(2) 装置をコンパクトにまとめられる。(2) The device can be compactly integrated.
(3) 常に一方の活性炭槽が開状態にある為、複数の
ドライクリーナの脱臭負荷に対しても対応出来る。(3) Since one activated carbon tank is always open, it can handle deodorizing loads of multiple dry cleaners.
第1図は本発明を実施するための溶剤ガス回収装置例を
示す概略構成図、第2図は本発明をドライクリーナに適
用したときの工程図、第3図は従来の単胴式溶剤ガス回
収装置の概略構成図、第4図は従来の双胴式溶剤ガス回
収装置の概略構成図、第5図は従来のドライクリーナ及
び単胴式と双胴式の溶剤ガス回収装置の各工程図であ
る。 図の主要部分の説明 1a,1b……活性炭 2a,2b……活性炭槽 7a,7b……出口ダンパ 8a,8b……入口ダンパ 9a,9b……脱着用蒸気入口弁 15a,15b……逆止弁FIG. 1 is a schematic configuration diagram showing an example of a solvent gas recovery apparatus for carrying out the present invention, FIG. 2 is a process diagram when the present invention is applied to a dry cleaner, and FIG. 3 is a conventional single-body type solvent gas. FIG. 4 is a schematic configuration diagram of a recovery device, FIG. 4 is a schematic configuration diagram of a conventional twin-body type solvent gas recovery device, and FIG. 5 is a process diagram of a conventional dry cleaner and a single-body type and double-body type solvent gas recovery device. Is. Explanation of the main parts of the figure 1a, 1b ...... Activated carbon 2a, 2b ...... Activated carbon tank 7a, 7b ...... Outlet damper 8a, 8b …… Inlet damper 9a, 9b …… Desorption steam inlet valve 15a, 15b …… Check valve
Claims (1)
着状態にあるとき、他槽の活性炭の脱着並びに活性炭乾
燥を行う溶剤ガスの回収装置において、溶剤ガスを発生
させる機器から送られてくる溶剤ガスに対し両槽の活性
炭を共に吸着状態におくことを特徴とする活性炭による
溶剤ガスの回収装置運転方法。1. A solvent gas recovery device for dividing activated carbon into two tanks and desorbing activated carbon from another tank and drying activated carbon when the activated carbon in one tank is in an adsorbed state. A method for operating a solvent gas recovery device using activated carbon, characterized in that both activated carbon in both tanks are placed in an adsorbed state with respect to the incoming solvent gas.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP20786988A JPH0796075B2 (en) | 1988-08-22 | 1988-08-22 | Method for operating solvent gas recovery device using activated carbon |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP20786988A JPH0796075B2 (en) | 1988-08-22 | 1988-08-22 | Method for operating solvent gas recovery device using activated carbon |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0255098A JPH0255098A (en) | 1990-02-23 |
| JPH0796075B2 true JPH0796075B2 (en) | 1995-10-18 |
Family
ID=16546898
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP20786988A Expired - Lifetime JPH0796075B2 (en) | 1988-08-22 | 1988-08-22 | Method for operating solvent gas recovery device using activated carbon |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0796075B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH08141282A (en) * | 1994-11-18 | 1996-06-04 | Tokyo Sensen Kikai Seisakusho:Kk | Solvent recovering mechanism in dry cleaner |
-
1988
- 1988-08-22 JP JP20786988A patent/JPH0796075B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0255098A (en) | 1990-02-23 |
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