JPS5892444A - Adsorptive removal of organic solvent gas - Google Patents
Adsorptive removal of organic solvent gasInfo
- Publication number
- JPS5892444A JPS5892444A JP56191364A JP19136481A JPS5892444A JP S5892444 A JPS5892444 A JP S5892444A JP 56191364 A JP56191364 A JP 56191364A JP 19136481 A JP19136481 A JP 19136481A JP S5892444 A JPS5892444 A JP S5892444A
- Authority
- JP
- Japan
- Prior art keywords
- air
- solvent gas
- adsorption
- relative humidity
- desorption
- 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.)
- Granted
Links
Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は、主として活性化炭素を吸着素材とし九吸脱曹
装置を利用して、例えば塗装ブースから排出されてくる
有機溶剤ガスを含有する空気から前記の有橋溶剤ガスを
吸着除去する方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention utilizes activated carbon as an adsorbing material and a nine-smoking desulfurizer to remove the bridged solvent from air containing organic solvent gas discharged from a painting booth, for example. This invention relates to a method for adsorbing and removing gas.
この種の有機溶剤ガス吸着除去方法において、被処理空
気からの有橋溶剤ガスの除去率を高くするには以下の条
件が必要とされていた。In this type of organic solvent gas adsorption removal method, the following conditions are required to increase the removal rate of bridged solvent gas from the air to be treated.
■ 空気の過度をできるだけ低くすること。■ Keep air excess as low as possible.
■ 空気の相対湿度をできるだけ低くすること。■ Keep the relative humidity of the air as low as possible.
しかし、塗装ブースにおいては、そこからの排気中に含
まれる塗料ミストが大気中に放出されることを防ぐため
に、排気を多量の水で洗浄して前記塗料ミストを除去す
る水洗処理が一般的に行なわれている。 そのため、こ
の様な―装ブースからの排気は相対湿度が約2S〜りj
llと非常に高く、従って、前記条件■から照らして有
機溶剤ガスの除去率を十分に高くすることができない欠
くがあった。However, in paint booths, in order to prevent the paint mist contained in the exhaust gas from being released into the atmosphere, a water washing process is generally used in which the exhaust gas is washed with a large amount of water to remove the paint mist. It is being done. Therefore, the relative humidity of the exhaust air from such a booth is approximately 2S.
Therefore, in light of the above-mentioned condition (2), the removal rate of organic solvent gas could not be made sufficiently high.
この様な除去率の低さに対し次の蟻な手段が考えられる
がいずれも欠課を有するものであつ九。The following methods can be considered to deal with such a low removal rate, but all of them have drawbacks.
■ 第1方法
吸着素材の吸着容量を増大すること、 このためには、
同一温度・同一相対湿度の被処理空気に対して@着票材
の量を大幅に増大するか若しくは、吸着素材の量は同一
にして脱着加熱空気の風量を増大する必要があるが、該
手段によると、何れの場合も脱着空気中における溶剤が
スW14度が低下し濃縮除去という初期の目的を十分に
達成しえないばかりか、曲者の場合は天竜の吸着素付シ
必要とするので設備費の増大が蕾しい欠点が有り、後者
の場合は、脱着加熱空気生成に対して膨大な熱エネルギ
ーを要し、ランニングコストの面での欠くが有る。■ The first method is to increase the adsorption capacity of the adsorption material.
For the air to be treated at the same temperature and relative humidity, it is necessary to significantly increase the amount of @adhesion material, or to increase the amount of desorption heated air while keeping the amount of adsorption material the same. According to the above, in both cases, the initial purpose of concentration and removal of the solvent in the desorption air decreases by 14 degrees, and not only does it fail to achieve the initial purpose of concentration and removal, but in the case of a curved person, it is necessary to use Tenryu's adsorbent. The drawback is that the equipment cost increases, and in the latter case, an enormous amount of thermal energy is required to generate desorption heated air, resulting in a shortfall in running costs.
(リ @コ方法
高湿実空気を吸脱着装置に通す前に除湿装置it K通
して除湿すること。(Rico method: Dehumidify high-humidity air by passing it through a dehumidifier IT K before passing it through an adsorption/desorption device.
この手段によるときは、除湿装置(凝縮型又は、吸収型
)の設置に伴なって、設備全体が複離化、大型化し易く
、かつ、イニシャルコストが膨大になるのみならず、除
湿装置の維持管理に手間を要し設備の運転効率、ひいて
は、塗装袋1d自体の生産性IkS化する欠点が有った
。When this method is used, the installation of a dehumidifier (condensation type or absorption type) tends to make the entire equipment more complex and larger, and the initial cost is enormous.In addition, the maintenance of the dehumidifier This has the drawback of requiring time and effort for management, reducing the operating efficiency of the equipment and, by extension, reducing the productivity of the coating bag 1d itself.
つまり、上記した従来方法の何れにおいても、高湿虜空
気から有機溶剤ガスを確実、十分に除去するKは、複雑
高価な装着を用いたシ、膨大な運転維持費を要するなど
、経済面で不利が強いられ、実用的方法とは言えないも
のであった。In other words, in any of the above-mentioned conventional methods, the ability to reliably and sufficiently remove organic solvent gas from high-humidity captive air requires complicated and expensive installations, requires enormous operation and maintenance costs, and is economically unsatisfactory. This method was disadvantageous and could not be called a practical method.
この様な実情に鑑み、本発明は、技術的にも、経済的か
らも極めて容易に実施し得ながら、高屋賓空気から有機
溶剤が7を確実、十分に除去しえる方法な提案すること
?目的とするものであって、1r#l溶剤ガスを含有す
る高相対湿度の常温空気を、約2〜7.50CId下に
加熱外温させたのち、吸駿8着装置の吸着域を通過させ
ることにより、前記有機溶剤ガスを空気から吸lW#!
去することな要旨とするものである。In view of these circumstances, the present invention proposes a method that can reliably and sufficiently remove organic solvents from takaya guest air, while being extremely easy to implement both technically and economically. For the purpose, room temperature air with high relative humidity containing 1r#l solvent gas is heated to an external temperature of about 2 to 7.50 CId, and then passed through the adsorption area of the adsorption device. By this, the organic solvent gas is drawn from the air.
This is a comprehensive summary.
即ち、塗装ブースから水洗処理されたのち排出される排
気のように、高相対湿度の有橋溶剤ガス含有空9にな、
吸脱着装置の吸着域に対し通過流動させる前に約2〜/
j’OJ!下に加熱外温するととKよシ、その空気の相
対湿度な低下することができ、かつ、このような加fI
p!!+湿に基づく相対湿度の低下から得られる、有機
溶剤ガスの吸着除去率の上昇量と、加熱昇温に基づく、
つtり、被処理空気温度の上昇に基づく吸着除去率の低
下瞼とは両者の比較において萌述の温度範囲での加熱外
温では)、外筺の方が上回っているのであり、従って、
高相対湿度、常温の空vCなそのまま吸wfl塚に対し
通過流動させる場合に比して、F−タル的に有機溶剤ガ
スの吸着除去率を高めることができる。 しかも、この
ような高相対湿度、常温の空気からの有機溶剤ガスの除
去率の低さを改善するために従来考えられていた既述■
及び■の方法に比べて本発明方法によれば、例えば後述
する前置ヒーターの如く構造的に簡単、小型で、かつ、
必要熱エネルギーも′儀かで済む小容量加熱装置を付加
するにけで良いから、吸脱着装置の複雑大形化、設備費
の高騰、i!には、ランニングコストの増大等といった
不利を招くことなく、経済面で非常に有利KsJ!施し
得るに至つ九のである。That is, when the air 9 containing bridged solvent gas has a high relative humidity, such as the exhaust gas discharged from a paint booth after being washed with water,
Approximately 2 to 30% of
j'OJ! When heated to a lower temperature, the relative humidity of the air can be lowered, and such an increase in fI
p! ! + The amount of increase in the adsorption removal rate of organic solvent gas obtained from the decrease in relative humidity due to humidity, and the increase in the adsorption removal rate due to heating and temperature increase,
In other words, when comparing the two, the reduction in adsorption removal rate due to an increase in the temperature of the air to be treated (at external heating temperatures in the temperature range mentioned above) is greater in the case of the outer casing, and therefore,
Compared to the case of flowing directly through an empty vC at high relative humidity and room temperature, the rate of adsorption and removal of organic solvent gas can be increased in terms of F-tal. Moreover, in order to improve the low removal rate of organic solvent gas from air with high relative humidity and room temperature, the previously mentioned
Compared to methods (1) and (2), the method of the present invention is structurally simpler and smaller, such as the preheater described later, and
Since all you have to do is add a small-capacity heating device that requires less heat energy, the adsorption/desorption device becomes more complicated and larger, and equipment costs soar. KsJ! is extremely advantageous from an economic point of view, without causing disadvantages such as increased running costs. There are nine things that can be done.
以上要するに、本発明は吸脱着装置を利用した有機溶剤
ガスの吸着除去方法においては、その除去率が低下する
として採用されていなかつ九被処理空気の温度を、前述
の温度範囲で上昇させる手段をあえて採用することKよ
って、従来より呻く要望されながら達成しえなかった或
いは、達成するためには多大な経済ロスを招くことにな
っていた高相対湿度常温空気からの有機剤ガスの除去率
向上を経済的に達成できるに至ったのである。In summary, the present invention provides a means for increasing the temperature of the air to be treated within the above-mentioned temperature range, which has not been adopted in the adsorption/removal method of organic solvent gas using an adsorption/desorption device because the removal rate would decrease. By intentionally adopting this method, we can improve the removal rate of organic gases from high relative humidity room temperature air, which has been a long-awaited goal but could not be achieved, or would incur a huge economic loss if it were to be achieved. It has now become possible to achieve this economically.
なお、本発明による除去率の向上を明らかにするために
、第6図に上記温度範囲と温度範囲外とにおける特定除
去率における被吸着空気量QA/説着空気量Qm−Mの
相違をグラフで示す。In order to clarify the improvement in the removal rate according to the present invention, FIG. 6 is a graph showing the difference in adsorbed air amount QA/adsorbed air amount Qm-M at a specific removal rate between the above temperature range and outside the temperature range. Indicated by
次に本発明の実施例をそれに使用する装置とともに説明
する。Next, an embodiment of the present invention will be described together with a device used therein.
第1実施例(第1図参照)
(1)は、塗装ブースであって、その底部に社、該ブー
ス(1)内の空気を水洗して塗料ミストを除去する水洗
装置(2)が設けられてあり、この水洗装置(2jを通
過して排出されるところの塗装ブースfi+の空気は相
対湿度が約25−25優、温度が夏期でコ!〜JJ00
、冬期で//〜コJ”Oとなっている。The first embodiment (see Fig. 1) (1) is a painting booth, and a water washing device (2) is installed at the bottom of the booth (1) to wash the air inside the booth (1) with water and remove paint mist. The air in the painting booth fi+, which passes through this water washing device (2j) and is discharged, has a relative humidity of about 25-25% and a temperature of about 100,000 in the summer!~JJ00
, in the winter//~ko J”O.
(3)は前置ヒータであって、前記排出空気な約2〜/
J00以下に加熱昇温するものであり、この前置ヒータ
((転)としては、一般に空気加熱用とし2て汎用され
ている¥に9ICヒータ又は温水ヒータな使用する。(3) is a pre-heater, and the exhaust air is approximately 2 to 1/2
The temperature is raised to below J00, and as this pre-heater, a 2-9 IC heater or a hot water heater, which is generally used for air heating, is used.
fc#′i7 イ14# −’?”、?+ラッテ前F3
tlNlヒ−pts>の上流に設けられてあって、前記
排出空気(A)中に残留している微小なミスFを除去す
るものである。fc#'i7 i14# -'? ”,?+F3 in front of Latte
It is provided upstream of the tlNl heapts> to remove minute mistakes F remaining in the discharged air (A).
(5)は吸脱着装置であって、活性化炭素職雑ヤ活性化
炭素粉粒体を他の繊維と混抄して紙状にしたものを筒状
のへ二カム状ローJ(6)に組立て、このロータ(6)
をその中心線R17で一定方向に回転する駆動装置()
)を験け、このロータ(6)を、その吸着域(61)が
前記前置と−タ(3)を通過し九排出空気(A)の通過
経路に位置し、かつ、その説着域(6b)が脱着用高温
空気(均の通過経路に位置する状1!IK配置して、そ
の位置での回転に伴ない連続的に吸脱着作用を行なうも
のである。 尚、この吸脱着装置(6)の具体構造は当
業者において一般に周知なものであるからこれ以上の詳
しい説明は省略する。(5) is an adsorption/desorption device in which activated carbon powder and activated carbon powder are mixed with other fibers and made into paper, and then transferred to a cylindrical hemi-cam-shaped row J (6). Assemble this rotor (6)
A drive device () that rotates in a fixed direction about its center line R17
), the rotor (6) is arranged such that its adsorption area (61) is located in the passage path of the discharged air (A) passing through the front and rear rotors (3), and its adsorption area is (6b) is a device in which the high temperature air for desorption (1!IK) is placed in the path of passage of the hot air, and the adsorption and desorption action is performed continuously as it rotates at that position.This adsorption and desorption device Since the specific structure of (6) is generally well known to those skilled in the art, further detailed explanation will be omitted.
(8)は脱着用空気加熱処理装置であって、次の構成を
有している。(8) is an air heating treatment device for desorption, and has the following configuration.
前記吸脱着装R(5iを通過した脱着用空気は第1熟交
換器(9)の加熱側を通って加熱され、この加熱され九
悦着用空気は、触媒酸化装置(11に供給され、この触
媒酸化装置+1(lにおいて溶剤ガスは触媒燃焼されて
脱臭処理される。 そして、脱臭処理後の脱着用空気け
、前記第1熱交換器(9)の被熱側を通って前記脱着用
空気(B)の予熱源として使用される。 そして、この
1gl熱交換器(9)を通った脱曽空* (B)は、第
1熟交換器+It)の放熱側を通って外気へ排出させる
。 この第コ熱交換器(11)の加熱側には前記吸脱
着装置(6)に向う脱着用空X(Blを加熱するもので
、この被加熱空気はフィルタ(1カを通って浄化された
外気である。The desorption air that has passed through the adsorption/desorption equipment R (5i) passes through the heating side of the first heat exchanger (9) and is heated, and this heated air for desorption is supplied to the catalytic oxidation device (11), In the catalytic oxidizer +1 (l), the solvent gas is catalytically combusted and deodorized.Then, the deodorizing air passes through the deodorizing air vent and the heated side of the first heat exchanger (9) after the deodorizing treatment. (B) is used as a preheating source for heat exchanger (B). The de-aired air (B) that has passed through this 1gl heat exchanger (9) is discharged to the outside air through the heat dissipation side of the first mature exchanger + It). The heating side of this primary heat exchanger (11) is for heating the desorption air X (Bl) facing the adsorption/desorption device (6), and this heated air is purified through a filter (1). It was fresh air.
θ鴫は咄記第2熱交換器(川を迂回するパイ/<ス路で
あって、前記第コ熱交換器(11) Icよる加#P1
作用によって脱着用に適した温度に調整するための屯の
である。θ is the second heat exchanger (the path that bypasses the river, and the heat exchanger (11) is added by Ic #P1
The temperature is adjusted to the temperature suitable for desorption by action.
(1番は前記餉媒酸化装置−内に設けた予熱用バーナで
ある。 QIFi触謀である。 この様にして、脱着用
空gL@を燃焼脱臭するとともに1その燃焼脱臭にて生
じた熱を脱着用空気(至)の加熱用に利用してあゐ。
なお、上記%部の具体的構造は周知であゐから、これ以
上詳しい説明は省略する。(No. 1 is the preheating burner installed in the above-mentioned oxidizing device. This is a QIFi catalyst. In this way, the air for desorption (gL) is burned and deodorized, and 1. the heat generated by the combustion deodorization is is used to heat the air for desorption.
Incidentally, since the specific structure of the above-mentioned % part is well known, further detailed explanation will be omitted.
該実施例の装置による実験結果を第6図に示す。The experimental results using the apparatus of this example are shown in FIG.
第6図のグツ7において縦軸はロータ(6)の吸着域(
6虐)を単位時間操り通過する風量QAと同ロータ(6
)の説着域(6b)を単位時間操)通過する風量喝の比
、りt)、渦纏比Mt−示す。(QJ−M)Q。In the shoe 7 in Fig. 6, the vertical axis is the adsorption area (
The air volume QA passing through the same rotor (6
The ratio of the air volume passing through the persuasion area (6b) of ) per unit time, Rt), and the vortex convergence ratio Mt- are shown. (QJ-M)Q.
同横軸Fi前記前置ヒータ(1) Kよって加熱され九
被吸着空鬼の温RTC’C>変化を示す。The same horizontal axis Fi shows the change in the temperature RTC'C of the air body heated by the preheater (1) and K to be adsorbed.
■ 同グラフ中線■は次の条件設定における実験結果を
示す、
QA寓/JoO婦4
t6s+wJコ℃ 〔加熱前温度〕除去前有機溶剤
ガス澁度= / 00 PPm除去後有機溶剤ガス一度
−W、Jppvn除去率v −ys、sチ
前置し−タ加熱前相対温度−104
脱着9気の吸着域供給温度−/コO℃
有機ガスはトルエンを主成分とする。■ The middle line ■ in the same graph indicates the experimental results under the following condition settings. , Jppvn removal rate v -ys, schi pre-heating relative temperature - 104 desorption adsorption zone supply temperature - / 0°C The organic gas has toluene as its main component.
■ 同グラブ中線■は次の条件設定における実験結果を
示す。■ The middle line ■ in the same graph indicates the experimental results under the following condition settings.
QA−/JOOWe/k
to謡 J/”C
x = J J P/V C絶対湿度〕除去ll1w*
溶剤ガス濃度−/ 7 J pprn除去後有機溶剤ガ
ス濃度−10,Oppm除去率ダー!0−
1IKI置ヒ一ク加熱前相対濃度−1σ−とする。QA-/JOOWe/k to song J/”C x = J JP P/V C absolute humidity] removal ll1w*
Solvent gas concentration - / 7 J Organic solvent gas concentration after pprn removal -10, Oppm removal rate is low! 0-1IKI set relative concentration before heating -1σ-.
■ 同グラス中線のは次の条PP設定における実験結果
を示す。■ The middle line in the same glass shows the experimental results for the following PP settings.
QAロ/コ00nd/に
16; j Q ℃
除責亭ダー!l−
1置ヒ一タ加熱曽相対湿度閣りS、 S %第、2実施
例(第3図参照)
前記前置ヒータ(mlを間接熱交換器とし、この加熱@
に前記11Ila交換S tS+と第J熱交換器(6)
との間の脱着用空気を一部通過させ、脱着用9気の燃焼
脱臭によ1生じた熱量を被吸着処理9気の加熱昇温に8
Mし九ものである。 その他Fi前記第1実施例と同様
のa威とする。 なお、第J熱交換器(llt−通過し
虎説着空気の一部を前記前置ヒータillである熱交換
器の加熱側を通すのも良い。QAro/ko00nd/ni 16; j Q ℃ Exorcist! 1-1 heating with relative humidity S, S % 1st, 2nd example (see Figure 3) The preheater (ml is an indirect heat exchanger, this heating @
11Ila exchange S tS+ and J heat exchanger (6)
A part of the air for desorption is passed through between the 9 gases for desorption, and the amount of heat generated by the combustion deodorization of 9 gases for desorption is used to raise the temperature of the adsorbed gas.
M is nine things. Other values are the same as in the first embodiment. In addition, it is also good to pass a part of the air that passes through the Jth heat exchanger (llt) and arrives at the heating side of the heat exchanger that is the preheater Ill.
第J実施例(1118図参照)
脱着用空気加熱処理装置(8)を以下の通シに構成する
。 その他は前記!/!!施例と同様な構成とする。Embodiment J (see Figure 1118) The air heating treatment device for desorption (8) is configured as follows. Others are mentioned above! /! ! The configuration is similar to that of the example.
フィルタ0曖を通った外4!PcIk1111I接熱交
換器0ηの加熱側(通し、次にヒータ0樽を通して前記
吸脱端装置i! f6+の説着域を通過させ、次に前記
間接熱交換器07)の吸熱側を通ってクーラ09)に入
り、そして、溶剤回収装置軸に入って、溶剤ガス等を液
化して分離回収するように構吠する。Out of the filter 0 vague! The heating side of the PcIk1111I indirect heat exchanger 0η (passed through, then passed through the adsorption area of the adsorption/removal end device i!f6+ through the heater 0 barrel, and then the heat absorption side of the indirect heat exchanger 07) 09), and enters the solvent recovery equipment shaft to liquefy and separate and recover the solvent gas, etc.
上記各部の構造については、夫々肩知であシ、これ以上
の詳しい説明は省略する。The structures of each of the above-mentioned parts are well known, and further detailed explanation will be omitted.
第y実施例(第壱図参照)
前記第j*施例のもの1でおいて、その前置ヒータ(3
)を間接熱交換器とし、その吸熱側に前記処理装置(8
)の熱交換器0ηからクーツ(19)闇における脱着空
気の一部なバイパスさせること。 その他は前記第j’
j!施例と同様とする。Yth embodiment (see Figure 1) In the j*th embodiment 1, the front heater (3
) is used as an indirect heat exchanger, and the treatment device (8
) to partially bypass the desorbed air in Coutts (19) darkness from the heat exchanger 0η. Others are the above j'
j! Same as the example.
前記の各!i!施例において、以下の一つ又は複数の組
合せ構成して実施するも幽い。Each of the above! i! In the embodiment, it is possible to configure and implement one or more of the following combinations.
■ 前記ロータ(6)に対する空気の通過方向を半径方
向とすること。(2) The direction in which air passes through the rotor (6) is the radial direction.
■ 前記吸脱着装置+ilを前記のような連続吸脱着式
のものでなく、被吸着空気と脱着空気とを吸脱着素材の
社iつた搭内に変互Kt#給して吸脱着するいわゆるバ
ッチ式のものとすること。■ The adsorption/desorption device +il is not a continuous adsorption/desorption type as described above, but a so-called batch adsorption/desorption device in which adsorbed air and desorbed air are alternately supplied to a chamber made of adsorption/desorption material. It should be of the ceremony.
■ 前記前1ヒータ(3)を、バーナ加熱式とすること
。(2) The front 1 heater (3) is of a burner heating type.
■ 前記脱着用空気加熱処理装置(8)の燃焼脱臭につ
いては、融媒燃焼に限らずバーナ燃焼とすること。(2) Combustion deodorization in the air heating treatment device for desorption (8) is not limited to melt combustion, but burner combustion should be used.
図面は本発明に係る有機溶剤ガス張着除去方法の実施の
態様な例示し、第1図はv/I、/寮施例を示すフロー
チャート、第8図は第コ実施例な示すフローチャート、
第8図は第jlil施例な示すフローチャート、第働図
は第ダ寮施例を示すフローチャート、第6図は実験結果
を示すグラフである。
(5:・・・・・・吸脱着装置
第2図
第3図The drawings illustrate embodiments of the organic solvent gas adhesion removal method according to the present invention, FIG. 1 is a flowchart showing the v/I/dormitory example, and FIG. 8 is a flowchart showing the co-embodiment.
FIG. 8 is a flowchart showing the first example, FIG. 8 is a flowchart showing the second example, and FIG. 6 is a graph showing the experimental results. (5:... Adsorption/desorption device Figure 2 Figure 3
Claims (1)
〜/j”0以下に加熱昇温させ九のち、吸脱着装置(6
)の吸着域を通過させることによ多、前記有機溶剤ガス
を空気から吸着除去する有機flj〜1ガス吸曹除夫方
法。Air at room temperature with high relative humidity containing organic solvent gas is
~/j" Heating and raising the temperature to below 0, after 9 days, an adsorption/desorption device (6
) A method for removing organic gas by adsorption and removing the organic solvent gas from the air by passing it through an adsorption zone.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56191364A JPS5892444A (en) | 1981-11-27 | 1981-11-27 | Adsorptive removal of organic solvent gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP56191364A JPS5892444A (en) | 1981-11-27 | 1981-11-27 | Adsorptive removal of organic solvent gas |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5892444A true JPS5892444A (en) | 1983-06-01 |
JPH0155888B2 JPH0155888B2 (en) | 1989-11-28 |
Family
ID=16273343
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP56191364A Granted JPS5892444A (en) | 1981-11-27 | 1981-11-27 | Adsorptive removal of organic solvent gas |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5892444A (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS62132523A (en) * | 1985-12-06 | 1987-06-15 | Toyobo Co Ltd | Method and device for adsorbing and removing gaseous halogenohydrocarbon |
JP2002159821A (en) * | 2000-11-28 | 2002-06-04 | Seibu Giken Co Ltd | Organic gas concentration apparatus |
JP2004105807A (en) * | 2002-09-13 | 2004-04-08 | Toyobo Co Ltd | Equipment for treating organic solvent |
JP2009160583A (en) * | 2009-04-20 | 2009-07-23 | Toyobo Co Ltd | Method for treating organic solvent gas |
JP2012115721A (en) * | 2010-11-29 | 2012-06-21 | Honda Motor Co Ltd | Exhaust gas treating apparatus |
CN105597490A (en) * | 2014-11-20 | 2016-05-25 | 杰智环境科技股份有限公司 | Organic exhaust gas adsorption/desorption, concentration and purifying system and method thereof |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109012013A (en) * | 2018-06-22 | 2018-12-18 | 佛山市墺林环保科技有限公司 | A kind of method and device of exhaust gas desorption condensing recovery |
CN109012014A (en) * | 2018-06-22 | 2018-12-18 | 佛山市墺林环保科技有限公司 | A kind of method and device of exhaust gas active-carbon adsorption desorption condensing recovery |
-
1981
- 1981-11-27 JP JP56191364A patent/JPS5892444A/en active Granted
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS62132523A (en) * | 1985-12-06 | 1987-06-15 | Toyobo Co Ltd | Method and device for adsorbing and removing gaseous halogenohydrocarbon |
JP2002159821A (en) * | 2000-11-28 | 2002-06-04 | Seibu Giken Co Ltd | Organic gas concentration apparatus |
JP2004105807A (en) * | 2002-09-13 | 2004-04-08 | Toyobo Co Ltd | Equipment for treating organic solvent |
JP2009160583A (en) * | 2009-04-20 | 2009-07-23 | Toyobo Co Ltd | Method for treating organic solvent gas |
JP2012115721A (en) * | 2010-11-29 | 2012-06-21 | Honda Motor Co Ltd | Exhaust gas treating apparatus |
CN105597490A (en) * | 2014-11-20 | 2016-05-25 | 杰智环境科技股份有限公司 | Organic exhaust gas adsorption/desorption, concentration and purifying system and method thereof |
Also Published As
Publication number | Publication date |
---|---|
JPH0155888B2 (en) | 1989-11-28 |
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