JPS62132523A - Method and device for adsorbing and removing gaseous halogenohydrocarbon - Google Patents

Method and device for adsorbing and removing gaseous halogenohydrocarbon

Info

Publication number
JPS62132523A
JPS62132523A JP60275466A JP27546685A JPS62132523A JP S62132523 A JPS62132523 A JP S62132523A JP 60275466 A JP60275466 A JP 60275466A JP 27546685 A JP27546685 A JP 27546685A JP S62132523 A JPS62132523 A JP S62132523A
Authority
JP
Japan
Prior art keywords
gas
adsorption
activated carbon
dehumidifier
halogenohydrocarbon
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
Application number
JP60275466A
Other languages
Japanese (ja)
Other versions
JPH0622654B2 (en
Inventor
Susumu Asakura
進 朝倉
Takeshi Kishimoto
岸元 武士
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toyobo Co Ltd
Original Assignee
Toyobo Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Toyobo Co Ltd filed Critical Toyobo Co Ltd
Priority to JP60275466A priority Critical patent/JPH0622654B2/en
Publication of JPS62132523A publication Critical patent/JPS62132523A/en
Publication of JPH0622654B2 publication Critical patent/JPH0622654B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Abstract

PURPOSE:To efficiently adsorb and remove gaseous halogenohydrocarbon from a gaseous mixture by dry-treating the gaseous mixture before the adsorption treatment due to activated carbon and regulating the relative humidity to a specified value or below. CONSTITUTION:After sending a gaseous mixture G contg. gaseous halogenohydrocarbon to a dehumidifier 2a packed with a drying agent and drying it herein till relative humidity is made to <=50%, it is sent to an adsorption tower 1a packed with activated carbon to remove gaseous halogenohydrocarbon and discharged to the outside of a system as purified gas. When the adsorption amount of water content in the inside of the dehumidifier 2a is saturated and drying capacity is reduced, the drying agent is regenerated by changing over an adsorption removal line L to a dehumidifier 2b side and sending hot air into the dehumidifier 2a through the regeneration line Lb of the drying agent. The gaseous mixture is continuously dried by repeating such the switching of such a valve. When the absorption tower 1a reaches nearly a saturated state, the introduction line of dry gas is changed over to the adsorption tower 1b side and the gas for desorption is sent to the adsorption tower 1a side through the regeneration line La of the absorbent to regenerate activated carbon.

Description

【発明の詳細な説明】 [a業上の利用分野] 太不日日8寸 ハロゲンイヒ岸イに7し去′:i、Hフ
ル今友する混合ガスから該ハロゲン化炭化水素系ガス(
以下Ha 1−CHガスと記す)を効率良く吸着除去す
ることのできる方法及び装置に関するものである。
[Detailed description of the invention] [Field of industrial application] From the mixed gas to the halogenated hydrocarbon gas (i, H full)
The present invention relates to a method and apparatus capable of efficiently adsorbing and removing Ha 1-CH gas (hereinafter referred to as Ha 1-CH gas).

[従来の技術] 有機溶剤を取扱う業界でしばしば問題となるのは揮発溶
剤が作業員に与える健康障害である。この為最近では有
機溶剤取扱い建屋の建設に当たって排気ダクトの完備が
義務付けられており、且つ大気中への溶剤蒸気の放散を
防止する為溶剤吸着除去設備の付設も要請されている。
[Prior Art] In industries that handle organic solvents, health problems caused by volatile solvents to workers are often a problem. For this reason, in recent years, when constructing a building that handles organic solvents, it has become mandatory to be equipped with exhaust ducts, and it has also been requested to install solvent adsorption and removal equipment to prevent the dissipation of solvent vapor into the atmosphere.

この様な溶剤吸着除去に最も広く実用化されている吸着
剤は活性炭であり1.普通は併設された2基以上の吸着
塔に活性炭を充填しておき、バルブ操作によって吸着と
脱着再生を交互に繰り返すことによって溶剤の吸着除去
を連続的に行なっている。
The most widely used adsorbent for solvent adsorption and removal is activated carbon.1. Normally, two or more adsorption towers installed side by side are filled with activated carbon, and adsorption and desorption regeneration are alternately repeated by valve operation, thereby continuously adsorbing and removing the solvent.

[発明が解決しようとする問題点] ところがフレオン(商品名、米国デュポン社製)や塩化
メチレン、四塩化炭素、クロロホルム等に代表される低
沸点(特に沸点100℃以下)のHa 1−CHガスは
吸着剤に対する吸着性が乏しく、多くのHa 1−CH
ガスが未吸着のままで放出され作業雰囲気や大気汚染を
引き起こすという問題がある。
[Problems to be solved by the invention] However, Ha 1-CH gas with a low boiling point (particularly a boiling point of 100°C or less) such as Freon (trade name, manufactured by DuPont, USA), methylene chloride, carbon tetrachloride, chloroform, etc. has poor adsorption to adsorbents, and many Ha 1-CH
There is a problem that the gas is released without being adsorbed, causing pollution of the working atmosphere and air.

即ち上記の様なHal−CHガスは冷媒、溶剤、抽出剤
、エローゾル噴霧剤等として広範囲の用途を有しており
、引火性を有していないという利点もあって利用範囲は
多岐に亘っているが、揮発性に富むものであるから雰囲
気汚染を生じ易く、各種吸着剤に対する吸着性が乏しい
こともあフてその除去に苦慮しているのが実情である。
In other words, Hal-CH gas as mentioned above has a wide range of uses as a refrigerant, solvent, extractant, aerosol spray agent, etc., and has the advantage of not being flammable, so it can be used in a wide range of applications. However, since it is highly volatile, it tends to pollute the atmosphere, and its poor adsorption to various adsorbents makes it difficult to remove it.

本発明はこの様な状況のもとで、Ha 1−CHガスを
含む混合ガスからHa 1−CHガスを効率良く吸着除
去することのできる方法及び装置を提供しようとするも
のである。
Under such circumstances, the present invention seeks to provide a method and apparatus capable of efficiently adsorbing and removing Ha 1-CH gas from a mixed gas containing Ha 1-CH gas.

c問題点を解決する為の手段] 本発明に係る吸着除去方法の構成は、Hal−CHガス
を含有する混合ガス中の該Hal−CHガスを活性炭に
よって吸着除去する方法において、吸着処理に先立ち前
記混合ガスを乾燥処理に付して相対湿度を50%以下と
しておくところに要旨を有するものである。また本発明
に係る吸着除去装設の構成とは、活性炭の充填された吸
着塔への前記混合ガス導入ラインに除湿装置を設けてな
るところに要旨を有するものである。
C. Means for Solving Problems] The configuration of the adsorption removal method according to the present invention is such that in the method of adsorbing and removing Hal-CH gas in a mixed gas containing Hal-CH gas using activated carbon, prior to the adsorption treatment, The gist is that the mixed gas is subjected to a drying process to keep the relative humidity at 50% or less. The gist of the structure of the adsorption removal equipment according to the present invention is that a dehumidifier is provided in the mixed gas introduction line to the adsorption tower filled with activated carbon.

[作用] 周知の様にHal−CHガスは吸着剤による吸着除去が
困難であるとされており、こうした傾向は吸看力の優れ
た活性炭を吸着剤として使用した場合も例外ではない。
[Function] As is well known, Hal-CH gas is difficult to adsorb and remove using an adsorbent, and this tendency is no exception even when activated carbon, which has excellent adsorption power, is used as an adsorbent.

そこでMal−CHガスが活性炭に吸着され難い理由を
明確にすべく色々の実験を繰り返すうち、次の様な事実
が明らかとなってきた。即ち活性炭は水分に対しても優
れた吸着能を有しており、水分とHal−CHガスは活
性炭吸着に関する限り拮抗的に作する。しかも一般的に
は水分の方が吸着され易いという傾向があった。従って
水分が一旦活性炭に吸着されるとHat−CHガスに対
する活性炭の吸着能が低下するばかりでなく、水分とH
at−CHガスの親和性が乏しいことがらHal−CH
ガスに対する吸着能は一段と乏しくなり、Ha 1−C
Hガス吸着除去の目的を果たし得なくなる。殊に我国は
温暖多湿気候であり、しかも四方が海に囲まれているこ
ともあって非常に湿度が高く室内外の湿度は年間を通じ
て殆んどが60%以上を示すと言われている。その為被
処理ガス中には相当量の湿気が混在しており、この湿気
が活性炭に優先的に吸着しHa 1−CHガスの吸着を
阻害しているものと考えられる。
Therefore, while various experiments were repeated to clarify the reason why Mal-CH gas is difficult to be adsorbed by activated carbon, the following facts became clear. That is, activated carbon has an excellent ability to adsorb moisture, and moisture and Hal-CH gas are antagonistic to each other as far as activated carbon adsorption is concerned. Moreover, there is a general tendency that water is more easily adsorbed. Therefore, once moisture is adsorbed on activated carbon, not only does the activated carbon's adsorption ability for Hat-CH gas decrease, but also the moisture and H
Hal-CH gas has poor affinity for at-CH gas.
The adsorption capacity for gas becomes even poorer, and Ha 1-C
The purpose of adsorption and removal of H gas cannot be achieved. In particular, our country has a warm and humid climate, and because it is surrounded by the ocean on all sides, it is extremely humid, with indoor and outdoor humidity reaching 60% or more throughout most of the year. Therefore, a considerable amount of moisture is mixed in the gas to be treated, and it is thought that this moisture preferentially adsorbs to the activated carbon and inhibits the adsorption of Ha 1-CH gas.

そこで本発明者等は、Hal−CHガスを含む混合ガス
を活性炭によって吸着除去するに先立って、該混合ガス
を予め乾燥・除湿してやればHa 1−CHガスの吸着
除去効率を高め得るのではなかろうかと考え、研究を進
めた。その結果該混合ガスを相対湿度が50%以下とな
るまで乾燥処理した後で活性炭に吸着させれば、Hal
−CHガスを極めて効率良く吸着除去し得ることが確認
された。
Therefore, the present inventors proposed that the efficiency of adsorption and removal of Ha 1-CH gas could be increased by drying and dehumidifying the mixed gas containing Hal-CH gas before adsorption and removal using activated carbon. I thought about it and proceeded with my research. As a result, if the mixed gas is dried until the relative humidity becomes 50% or less and then adsorbed on activated carbon, Hal
It was confirmed that -CH gas could be adsorbed and removed extremely efficiently.

ちなみに第1図は、Hal−CHガスとしてフレオン1
13 (CG12F −CClF2 )ガスを遭択して
活性炭による吸着実験を行ない、該Hal−CHガス含
有混合ガス(残部ガスは空気)の相対湿度がフレオン1
13及び水分の平衡吸着量にどの様な影響を及ぼすかを
調べた結果を示すものであり、実験法は下記の通りとし
た。
By the way, Figure 1 shows Freon 1 as Hal-CH gas.
13 (CG12F -CClF2) gas was selected and an adsorption experiment using activated carbon was conducted, and the relative humidity of the mixed gas containing Hal-CH gas (the remaining gas is air) was found to be Freon 1.
13 and the results of an investigation to determine the effect on the equilibrium adsorption amount of water, and the experimental method was as follows.

く実験法〉 (1)第2図に略示する如く100℃の透明密閉容器V
に下記無機塩の飽和水溶液Sを装入し、器内の調湿(a
t25℃)を行なう。
Experimental method> (1) As shown schematically in Figure 2, a transparent airtight container V at 100°C
The following saturated aqueous solution S of inorganic salt was charged into the container, and the humidity inside the container was adjusted (a
t25°C).

K2Co3飽和水溶液  =40% NLNO3飽和水溶液  :61〜64%(NH4) 
2504飽和水溶液=81〜83%(2)絶乾状態(1
20℃X3hr以上処理後)の活性炭(約2g)ACを
上記密閉容器V内へ入れ、飽和水分率となるまで吸着さ
せる。
K2Co3 saturated aqueous solution = 40% NLNO3 saturated aqueous solution: 61-64% (NH4)
2504 saturated aqueous solution = 81-83% (2) Absolutely dry state (1
Activated carbon (approximately 2 g) AC (after being treated at 20° C. for 3 hours or more) is placed in the sealed container V and adsorbed until it reaches a saturated moisture content.

(3)活性炭ACが飽和水分率に到達した後、該密閉容
器V内ニフレオン113を7.8g/lo。
(3) After the activated carbon AC reaches a saturated moisture content, 7.8 g/lo of Nifreon 113 is added to the sealed container V.

l注入し、攪拌機rにより攪拌して容器V内にフレオン
113を均一に分散させ(フレオン濃度10.300 
ppm)た後、約1時間放置する。
Freon 113 is injected into the container V and stirred with a stirrer R to uniformly disperse Freon 113 in the container V (Freon concentration 10.300
ppm) and then leave it for about 1 hour.

(4)その後密封容器V内の湿度及びフレオン113濃
度を測定し、初期濃度より減少して安定化したときの安
定化濃度を差引いて活性炭ACへの吸着量を求めた。
(4) Thereafter, the humidity and Freon 113 concentration in the sealed container V were measured, and the amount of adsorption on activated carbon AC was determined by subtracting the stabilized concentration when the concentration decreased from the initial concentration and stabilized.

(5)尚比較の為トルエンについても同様にして相対湿
度と平衡吸着量の関係を調べた。
(5) For comparison, the relationship between relative humidity and equilibrium adsorption amount was similarly investigated for toluene.

第1図からも明らかな様に相対湿度が50%以下である
場合Hat−CHガスはむしろ湿分よりも優先的に活性
炭に吸着されするが、相対湿度が50%を超えると湿分
の吸着量が急激に増大すると共にHal−CHガスの吸
着量は急激に低下してくる。こうした傾向からも明らか
な様に、Ha 1−CHガスは必ずしも活性炭に対する
吸着能が乏しいと言う訳ではなく、一定量以上の湿気の
存在によって活性炭に対する吸着能が激減するものと考
えられ、換言するとHat−CHガス混合ガスを予め乾
燥し相対湿度を低下させた後に活性炭による吸着処理を
行なえば、Hal−CHガスの効果的な吸着除去が可能
となる。尚トルエンについては、相対湿度による吸着量
の低減傾向が非常に小さいことが分かる。
As is clear from Figure 1, when the relative humidity is below 50%, Hat-CH gas is adsorbed onto activated carbon preferentially over moisture, but when the relative humidity exceeds 50%, moisture is adsorbed. As the amount of Hal-CH gas increases rapidly, the amount of Hal-CH gas adsorbed decreases rapidly. As is clear from these trends, Ha 1-CH gas does not necessarily have a poor adsorption capacity for activated carbon, but it is thought that the presence of moisture above a certain amount drastically reduces the adsorption capacity for activated carbon. By drying the Hat-CH gas mixture in advance to lower the relative humidity and then performing adsorption treatment with activated carbon, it becomes possible to effectively adsorb and remove the Hal-CH gas. Regarding toluene, it can be seen that the tendency for the amount of adsorption to decrease due to relative humidity is very small.

本発明はこうした知見を基になされたものであって、H
al −CHガスを含む混合ガスを活性炭により吸着除
去するに先立って、該混合ガスを乾燥゛するところに特
徴を有するものであって、乾燥の程度は第1図に示した
実験結果より、活性炭への水分の吸着量が急増する相対
湿度50%を基準として該値以下(より好ましくは40
%以下)と定めた。尚乾燥の手段はどの様なものであっ
てもよいが、連続処理という観点から最も好ましいのは
加熱乾燥或は除湿器や吸湿剤充填塔を通過させる方法で
ある。
The present invention is based on these findings, and H
This method is characterized by drying the mixed gas containing al-CH gas before it is adsorbed and removed by activated carbon, and the degree of drying is determined from the experimental results shown in Figure 1. Below the relative humidity (more preferably 40%), based on the relative humidity of 50% at which the amount of moisture adsorbed to the
% or less). Although any drying method may be used, the most preferred method from the viewpoint of continuous processing is heating drying or passing through a dehumidifier or a tower packed with a moisture absorbent.

また本発明に係る装置の構成は、活性炭充填塔の前記混
合ガス導入ラインに除湿装置を設け、上記のHa 1−
CHガス吸着除去法を円滑に遂行し得る様に構成したも
のであり、具体的な構成は設備の全状況や要求処理能力
等に応じて任意に設計変更することができるが、基本的
な構成を例示すると第3図に略示する通りである。即ち
第3図においてIa、lbは吸着塔を示し、内部には粒
状、繊維状、ハニカム状等の活性炭が充填されており、
また2a、2bは除湿器を示し内部には適当な乾燥剤が
充填されている。そして実線りで示すラインはHal−
CHガス吸着除去ライン、破線Laで示すラインは吸着
剤再生ライン、破線Lbで示すラインは乾燥剤再生ライ
ンを夫々示す。即ちHal−CHガスを含む混合ガスG
はラインLからバルブ操作により選定される一方の除湿
器2a(又は2b)へ送り込まれ、この部分で相対湿度
が50%以下となるまで乾燥された後、同様のバルブ操
作により選定される一方の吸着塔Ia(又はlb)へ送
給される。そして該吸着塔1a(又はlb)でHa 1
−CHガスの除去された混合ガスは浄化ガスとして系外
へ放出される。
Further, the configuration of the apparatus according to the present invention is such that a dehumidifying device is provided in the mixed gas introduction line of the activated carbon packed tower, and the above-mentioned Ha 1-
The system is designed to smoothly perform the CH gas adsorption removal method, and the specific configuration can be changed as desired depending on the overall situation of the equipment and the required processing capacity, but the basic configuration is An example of this is shown schematically in FIG. That is, in FIG. 3, Ia and lb indicate adsorption towers, the interior of which is filled with activated carbon in the form of granules, fibers, honeycombs, etc.
Further, 2a and 2b indicate dehumidifiers, the interior of which is filled with a suitable desiccant. And the solid line is Hal-
The CH gas adsorption removal line, the line indicated by the broken line La, indicates the adsorbent regeneration line, and the line indicated by the broken line Lb indicates the desiccant regeneration line, respectively. That is, mixed gas G containing Hal-CH gas
is sent from line L to one of the dehumidifiers 2a (or 2b) selected by operating the valve, and is dried in this section until the relative humidity becomes 50% or less. It is fed to adsorption tower Ia (or lb). In the adsorption tower 1a (or lb), Ha 1
The mixed gas from which the -CH gas has been removed is discharged to the outside of the system as a purified gas.

そして除湿器2a(又は2b)内の水分吸着量が飽和し
乾燥能力が低下してくると、吸着除去ラインLを除湿器
2b側へ切換える一方、除湿器2aには乾燥剤再生ライ
ンLbから熱風(又は乾燥空俺 1戸、:t h  :
s  z    古ζ拳品文+1+シ l→力t 1 
 起 −シLL 也4Mマ吏「Δ去して次回の乾燥工程
まで待機させ、この様なバルブ切換えを繰返すことによ
って混合ガスを連続的に乾燥する。また吸着塔Ia内の
Hal−CHガス吸着量が飽和状態に近ずくとHa 1
−CHガス吸着能が低下してくるので、乾燥ガスの導入
ラインを吸着塔1b側へ切換えて吸着除去を継続する一
方、吸着塔1a側には吸着剤再生ラインLaからHat
−CH脱着用のガス(通常は熱風)を送り込み、活性炭
に吸着しているHal−CHガスを脱着して活性炭を再
生すると共に、脱着排ガスは再生ラインLaの下流側へ
送って必要によりHal−CHガスの凝縮回収が行なわ
れる。こうした吸着剤による吸着除去と脱着再生を繰り
返すことによって、Hal−CHガスの吸着除去が連続
的に行なわれる。
When the amount of water adsorption in the dehumidifier 2a (or 2b) becomes saturated and the drying capacity decreases, the adsorption removal line L is switched to the dehumidifier 2b side, while the dehumidifier 2a is supplied with hot air from the desiccant regeneration line Lb. (or one dry sky, :th:
s z Ancient ζ fist article + 1 + shi l→power t 1
Ki-shiLL and 4M engineer: ``The mixed gas is dried continuously by removing the Δ and waiting until the next drying process, and repeating such valve switching.Also, the Hal-CH gas adsorption in the adsorption tower Ia When the amount approaches saturation, Ha 1
-CH gas adsorption capacity is decreasing, so the drying gas introduction line is switched to the adsorption tower 1b side to continue adsorption removal, while the adsorption tower 1a side is connected to the adsorption regeneration line La from the Hat
-CH desorption gas (usually hot air) is sent in to desorb the Hal-CH gas adsorbed on the activated carbon to regenerate the activated carbon, and the desorbed exhaust gas is sent to the downstream side of the regeneration line La for Hal-CH gas adsorbed on the activated carbon. CH gas is condensed and recovered. By repeating such adsorption removal and desorption regeneration using the adsorbent, adsorption and removal of Hal-CH gas is continuously performed.

尚吸着塔1a、1bの切換え時期は、吸着塔排出側ライ
ンにHa 1−CHガス濃度検知器を設けてその増加量
を検知することによりコントロールすればよく、この場
合切換えバルブを電磁バルブとし前記4度検知器と言値
的に環装して初漁λ日専期を自動制御することも勿論可
能である。また除湿器2a、2bについてもその排出側
ラインに湿度計を設けて乾燥能を連続的に検知すること
により再生工程への切換え時期を調整するのがよく、こ
の場合上記と同様電磁バルブと組合わせて全自動化する
ことも勿論可能である。第3図では2個1組の吸着塔1
a、lb及び除湿器2a、2bを切換え運転する構成の
ものを示したが、本発明はもとよりこうしたタイプのも
のに限定される訳ではなく、3個以上の吸着塔や除湿器
を併設して処理能力を高めたり、また処理ガス量が比較
的少量であるか或は処理ガスの発生時期が連続的でない
様な場合は、夫々1個の吸着塔及び除湿器によって吸着
除去を行ない、非処理期間中に脱着再生を行なう様にす
ることもできる。
The switching timing of the adsorption towers 1a and 1b may be controlled by installing a Ha 1-CH gas concentration detector on the adsorption tower discharge line and detecting the increase in the concentration. In this case, the switching valve is a solenoid valve and the Of course, it is also possible to automatically control the first fishing λ day exclusive period by linking the fish with a 4-degree detector. It is also best to install a hygrometer on the discharge line of the dehumidifiers 2a and 2b to continuously detect the drying capacity to adjust the timing of switching to the regeneration process. Of course, it is also possible to fully automate the process. In Figure 3, a set of two adsorption towers 1
Although a structure in which the a, lb and dehumidifiers 2a and 2b are switched and operated is shown, the present invention is not limited to this type, and it is possible to use a structure in which three or more adsorption towers or dehumidifiers are installed together. In order to increase the processing capacity, or when the amount of processed gas is relatively small or the timing of generation of processed gas is not continuous, adsorption removal is performed using one adsorption tower and one dehumidifier, and non-processed gas is removed. It is also possible to perform desorption and regeneration during the period.

[実施例] 第4図に示す実験装置を使用し、活性炭充填塔へ供給す
るガス中のフレオン113濃度及び湿度を色々変化させ
、所定時間吸着処理を行なった場合における活性炭充填
塔通過ガス中のフレオン113濃度の変化を調べた。即
ち第4図に示す如く模擬ガス発生装置4内のヒータ5上
に設置した蒸発皿6内にフレオン113を装入して加熱
蒸発させ、該蒸気を空気と共にライン8及びファン9を
通して吸着塔1a(又はlb)へ送り込む。このとき該
供給ガスに、調湿装置10及びヒータ11を通して加湿
又は除湿した空気を合流させて供給ガスの湿度を様々に
変化させさせるものとし、且つ吸着塔入側ガスの温度を
TCA、湿度をHCで夫々検知しつつヒータ11の上記
弁を開閉することによって供給ガスの温度及び湿度を調
整する。そして各条件毎に吸着塔1a(又はlb)通過
前・後におけるガス中のフレオン113?a度をハイド
ロカーボンメータXIによって調べた。
[Example] Using the experimental apparatus shown in Fig. 4, the Freon 113 concentration and humidity in the gas supplied to the activated carbon packed tower were variously changed, and the adsorption treatment was performed for a predetermined period of time. Changes in Freon 113 concentration were investigated. That is, as shown in FIG. 4, Freon 113 is charged into an evaporating dish 6 installed on a heater 5 in a simulated gas generator 4, heated and evaporated, and the vapor is passed along with air through a line 8 and a fan 9 to an adsorption tower 1a. (or lb). At this time, air that has been humidified or dehumidified is added to the supply gas through the humidity control device 10 and the heater 11 to variously change the humidity of the supply gas. The temperature and humidity of the supplied gas are adjusted by opening and closing the valves of the heater 11 while detecting them with the HC. And for each condition, which Freon 113 is in the gas before and after passing through the adsorption tower 1a (or lb)? The degree of a was checked using a hydrocarbon meter XI.

実験条件は下記の通りとした。The experimental conditions were as follows.

く実験条件〉 大気条件: 28℃、90% 原料ガス送給量: 14.48m’/分処理温度: 3
5〜40℃ 第5図は1パッチ目終了時における吸着塔通過ガス中の
フレオン113濃度と5バッチ目終了時における同ガス
中のフレオン113濃度を示したものであり、これらの
結果より次の様に考えることができる。
Experimental conditions> Atmospheric conditions: 28°C, 90% Raw material gas feed rate: 14.48 m'/min Processing temperature: 3
5-40℃ Figure 5 shows the Freon 113 concentration in the gas passing through the adsorption tower at the end of the first patch and the Freon 113 concentration in the same gas at the end of the fifth batch. Based on these results, the following You can think in different ways.

(1)供給ガスの湿度が50%を超えると、フレオン1
13濃度が高い場合はもとより、フレオン113?a度
が低い場合でも少ない処理回数で活性炭のフレオン吸着
活性が低下し、出口ガス中のフレオン113濃度は著し
く高くなっている。
(1) If the humidity of the supplied gas exceeds 50%, Freon 1
Not only when the 13 concentration is high, but Freon 113? Even when the degree of a is low, the Freon adsorption activity of the activated carbon decreases with a small number of treatments, and the Freon 113 concentration in the outlet gas becomes significantly high.

(2)これに対し供給ガスの湿度を50%以下に低下さ
せておくと出口ガス中のフレオン113濃度は初回吸着
処理時よりも5回の吸着処理を行なった後の方が低くな
っている。即ち本実験は約65%RHの外気雰囲気で実
験を行なったものであり、こうした条件のもとでは吸着
塔内の活性炭は若干吸湿しているものと考えられ、初回
吸着処理時は吸着水分の影響を受けて若干低めの吸着活
性しか発揮しないが、供給ガスの湿度を50%以下にし
ておくと、吸着塔内に充填された活性炭の吸着水分が供
給ガスの通過により逆に放出されて活性炭のフレオン1
13吸着活性が高まり、初回吸着処理時よりもむしろフ
レオン113吸着除去効率が同上してきたものと考えら
れる。何れにしても供給ガスの湿度を50%以下として
おくことによって、該供給ガス中のフレオン113を極
めて効率良く吸着除去することができる。
(2) On the other hand, if the humidity of the supplied gas is lowered to below 50%, the Freon 113 concentration in the outlet gas will be lower after 5 adsorption treatments than during the first adsorption treatment. . In other words, this experiment was conducted in an outside air atmosphere with a relative humidity of approximately 65%. Under these conditions, the activated carbon in the adsorption tower is thought to have absorbed some moisture, and during the initial adsorption treatment, the amount of adsorbed water was However, if the humidity of the supplied gas is kept below 50%, the moisture adsorbed by the activated carbon packed in the adsorption tower will be released as the supplied gas passes through the activated carbon. freon 1
It is considered that the Freon 113 adsorption activity increased and the Freon 113 adsorption removal efficiency became higher than that at the time of the initial adsorption treatment. In any case, by keeping the humidity of the supplied gas at 50% or less, Freon 113 in the supplied gas can be adsorbed and removed extremely efficiently.

[発明の効果コ 本発明は以上の様に構成されているが、要するにHat
−CHガスを含む混合ガスを予め除湿してその湿度を5
0%以下としておくことにより、活性炭のHal−CH
ガス吸着性能を最大限に発揮させることができ、Hal
−CHガスを効率良く吸着除去することができる。しか
もこの方法を実施する為の装置は、活性炭充填塔の処理
ガス導入ラインに除湿器を設けるだけでよく、既設の活
性炭吸着設備をそのまま活用することができるので設備
負担も少なくて済み、更には活性炭吸着塔及び除湿器を
夫々2基以上並設して吸着と脱着再生及び除湿と乾燥再
生を交互に行なう様にすればHa 1−CHガスの吸着
除去を連続化することもでき、従来より吸着除去が困難
であるとされていたHal−CHガスの吸着除去を効率
良く遂行し得ることになった。
[Effects of the Invention] Although the present invention is configured as described above, in short, Hat
- Dehumidify the mixed gas containing CH gas in advance to reduce its humidity to 5.
By keeping it below 0%, Hal-CH of activated carbon
Gas adsorption performance can be maximized, and Hal
-CH gas can be efficiently adsorbed and removed. Moreover, the equipment for carrying out this method requires only a dehumidifier to be installed in the treated gas introduction line of the activated carbon packed tower, and the existing activated carbon adsorption equipment can be used as is, reducing the equipment burden. If two or more activated carbon adsorption towers and two or more dehumidifiers are installed in parallel to perform adsorption and desorption regeneration and dehumidification and dry regeneration alternately, adsorption and removal of Ha 1-CH gas can be made continuous, which is faster than before. It became possible to efficiently adsorb and remove Hal-CH gas, which was considered difficult to adsorb.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は混合ガスの相対湿度がフレオン又はトルエンの
吸着活性に及ぼす影響を調べた結果を示すグラフ、第2
図は吸着活性試験法を示す説明図、第3図は本発明に係
る装置を例示する概略フロー図、第4図は実施例で用い
た装置を示す説明図、第5図は供給ガスの湿度と吸着塔
出口ガスのフレオン濃度変化を示すグラフである。 Ia、lb・・・活性炭充填塔 2a、2b・・・除湿器 L・・・Hal−CHガス吸着処理ラインLa・・・活
性炭脱着再生ライン Lb・・・除湿器再生ライン
Figure 1 is a graph showing the results of investigating the influence of the relative humidity of a mixed gas on the adsorption activity of freon or toluene.
The figure is an explanatory diagram showing the adsorption activity test method, Figure 3 is a schematic flow diagram illustrating the apparatus according to the present invention, Figure 4 is an explanatory diagram showing the apparatus used in the examples, and Figure 5 is the humidity of the supplied gas. 2 is a graph showing changes in Freon concentration in adsorption tower outlet gas. Ia, lb...Activated carbon packed towers 2a, 2b...Dehumidifier L...Hal-CH gas adsorption treatment line La...Activated carbon desorption and regeneration line Lb...Dehumidifier regeneration line

Claims (2)

【特許請求の範囲】[Claims] (1)ハロゲン化炭化水素系ガスを含有する混合ガス中
の該ハロゲン化炭化水素系ガスを活性炭によって吸着除
去する方法において、吸着処理に先立ち前記混合ガスを
乾燥処理に付して相対湿度を50%以下としておくこと
を特徴とするハロゲン化炭化水素系ガスの吸着除去方法
(1) In a method of adsorbing and removing a halogenated hydrocarbon gas in a mixed gas containing a halogenated hydrocarbon gas using activated carbon, the mixed gas is subjected to a drying process to reduce the relative humidity to 50% prior to the adsorption process. % or less.
(2)ハロゲン化炭化水素系ガスを含有する混合ガス中
の該ハロゲン化炭化水素系ガスを活性炭によって吸着除
去する装置であって、活性炭の充填された吸着塔への前
記混合ガス導入ラインに除湿装置を設けてなることを特
徴とするハロゲン化炭化水素系ガスの吸着除去装置。
(2) A device for adsorbing and removing halogenated hydrocarbon gas in a mixed gas containing halogenated hydrocarbon gas using activated carbon, the device being a dehumidifier to a line introducing the mixed gas to an adsorption tower filled with activated carbon. What is claimed is: 1. A device for adsorption and removal of halogenated hydrocarbon gas, characterized by comprising a device.
JP60275466A 1985-12-06 1985-12-06 Method for adsorption removal of halogenated hydrocarbon gas Expired - Lifetime JPH0622654B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60275466A JPH0622654B2 (en) 1985-12-06 1985-12-06 Method for adsorption removal of halogenated hydrocarbon gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60275466A JPH0622654B2 (en) 1985-12-06 1985-12-06 Method for adsorption removal of halogenated hydrocarbon gas

Publications (2)

Publication Number Publication Date
JPS62132523A true JPS62132523A (en) 1987-06-15
JPH0622654B2 JPH0622654B2 (en) 1994-03-30

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Country Link
JP (1) JPH0622654B2 (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06343823A (en) * 1993-06-08 1994-12-20 Nec Corp Intake and exhaust treatment system for clean chamber
WO1996030109A1 (en) * 1995-03-24 1996-10-03 Colcard Pty. Limited Refrigerant separation
US6597416B1 (en) 1999-03-29 2003-07-22 Seiko Epson Corporation Display panel with supporting member having recess for elastic connector
US6733570B2 (en) 1992-12-02 2004-05-11 Ebara Research Co., Ltd. Method and apparatus for the preparation of clean gases
KR100438486B1 (en) * 2001-03-12 2004-07-07 주식회사환경과생명 Industrial stench remove apparatus using cartridge type activated carborn fiber adsorber
JP2009503899A (en) * 2005-08-03 2009-01-29 インテグリス・インコーポレーテッド Transfer container
CN103768929A (en) * 2014-01-28 2014-05-07 上海黎明资源再利用有限公司 Purification treatment device for flue gas generated in garbage incineration process, and application of purification treatment device
CN103990364A (en) * 2014-03-02 2014-08-20 中国瑞林工程技术有限公司 Incineration flue gas treatment system and incineration flue gas treatment method
CN104258709A (en) * 2014-09-26 2015-01-07 成都中环资(集团)有限公司 Waste derived fuel burning smoke separation and purifying process

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JPS5164472A (en) * 1974-12-03 1976-06-03 Shozo Tamura Kunjogasunokaishu shorihoho
JPS51110200A (en) * 1975-03-24 1976-09-29 Hitachi Ltd JUKYOSO JOKYO SOCHI
JPS5628888A (en) * 1979-08-17 1981-03-23 Mitsubishi Paper Mills Ltd Noncarbon transfer paper
JPS5892444A (en) * 1981-11-27 1983-06-01 Taikisha Ltd Adsorptive removal of organic solvent gas
JPS606626A (en) * 1983-06-24 1985-01-14 Toho Kako Kensetsu Kk Recovery of low-boiling solvent

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5164472A (en) * 1974-12-03 1976-06-03 Shozo Tamura Kunjogasunokaishu shorihoho
JPS51110200A (en) * 1975-03-24 1976-09-29 Hitachi Ltd JUKYOSO JOKYO SOCHI
JPS5628888A (en) * 1979-08-17 1981-03-23 Mitsubishi Paper Mills Ltd Noncarbon transfer paper
JPS5892444A (en) * 1981-11-27 1983-06-01 Taikisha Ltd Adsorptive removal of organic solvent gas
JPS606626A (en) * 1983-06-24 1985-01-14 Toho Kako Kensetsu Kk Recovery of low-boiling solvent

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6733570B2 (en) 1992-12-02 2004-05-11 Ebara Research Co., Ltd. Method and apparatus for the preparation of clean gases
US6911064B2 (en) 1992-12-02 2005-06-28 Ebara Research Co., Ltd. Method and apparatus for the preparation of clean gases
US7029518B2 (en) 1992-12-02 2006-04-18 Ebara Research Co., Ltd. Method and apparatus for the preparation of clean gases
JPH06343823A (en) * 1993-06-08 1994-12-20 Nec Corp Intake and exhaust treatment system for clean chamber
WO1996030109A1 (en) * 1995-03-24 1996-10-03 Colcard Pty. Limited Refrigerant separation
US6597416B1 (en) 1999-03-29 2003-07-22 Seiko Epson Corporation Display panel with supporting member having recess for elastic connector
KR100438486B1 (en) * 2001-03-12 2004-07-07 주식회사환경과생명 Industrial stench remove apparatus using cartridge type activated carborn fiber adsorber
JP2009503899A (en) * 2005-08-03 2009-01-29 インテグリス・インコーポレーテッド Transfer container
CN103768929A (en) * 2014-01-28 2014-05-07 上海黎明资源再利用有限公司 Purification treatment device for flue gas generated in garbage incineration process, and application of purification treatment device
CN103768929B (en) * 2014-01-28 2016-04-27 上海黎明资源再利用有限公司 The purifying processing device of the flue gas produced in a kind of Refuse Incineration Process and application thereof
CN103990364A (en) * 2014-03-02 2014-08-20 中国瑞林工程技术有限公司 Incineration flue gas treatment system and incineration flue gas treatment method
CN104258709A (en) * 2014-09-26 2015-01-07 成都中环资(集团)有限公司 Waste derived fuel burning smoke separation and purifying process

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