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JP2909253B2 - How to concentrate chlorine gas - Google Patents
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JP2909253B2 - How to concentrate chlorine gas - Google Patents

How to concentrate chlorine gas

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Publication number
JP2909253B2
JP2909253B2 JP3141776A JP14177691A JP2909253B2 JP 2909253 B2 JP2909253 B2 JP 2909253B2 JP 3141776 A JP3141776 A JP 3141776A JP 14177691 A JP14177691 A JP 14177691A JP 2909253 B2 JP2909253 B2 JP 2909253B2
Authority
JP
Japan
Prior art keywords
chlorine
gas
adsorption tower
adsorption
adsorbent
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
Application number
JP3141776A
Other languages
Japanese (ja)
Other versions
JPH04367503A (en
Inventor
照夫 平山
慎司 竹中
国博 山田
嘉嗣 神野
洋之 伊藤
功 菊地
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.)
Mitsui Chemicals Inc
Original Assignee
Mitsui Chemicals Inc
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 Mitsui Chemicals Inc filed Critical Mitsui Chemicals Inc
Priority to JP3141776A priority Critical patent/JP2909253B2/en
Publication of JPH04367503A publication Critical patent/JPH04367503A/en
Application granted granted Critical
Publication of JP2909253B2 publication Critical patent/JP2909253B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Separation Of Gases By Adsorption (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は圧力スイング吸着法を利
用する塩素の濃縮方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for concentrating chlorine using a pressure swing adsorption method.

【0002】[0002]

【従来の技術】塩素は非常に重要な工業中間原料で多く
の化学産業で使用されており、各所に塩素の分離のため
の設備が存在する。従来、塩素を含むガスより塩素を分
離する方法としては、ガスを加圧・冷却して液体塩素と
しガスより分離する方法や、塩素系有機溶剤に塩素を吸
収させた溶剤をストリッピングすることにより塩素を分
離する方法が知られている。
BACKGROUND OF THE INVENTION Chlorine is a very important industrial intermediate and is used in many chemical industries, and there are facilities for chlorine separation in various places. Conventionally, to separate chlorine from gas containing chlorine, pressurizing and cooling the gas to form liquid chlorine and separating it from the gas, or by stripping the solvent in which chlorine is absorbed by a chlorine-based organic solvent Methods for separating chlorine are known.

【0003】しかし、前者の方法は高圧ガスを取り扱う
ので、高価で保守管理の面倒なガス圧縮機や冷凍設備な
どが必要となり、特に塩素濃度の比較的低いガスより塩
素を分離する場合には、非常な高圧または極低温による
操作となり、設備費が増大する。また後者の方法は、通
常溶剤として四塩化炭素を使用するが、昨今のフロンガ
スによる環境問題により四塩化炭素の使用が禁止される
方向にあり、将来有効な方法と言えなくなった。
However, the former method uses a high-pressure gas, and therefore requires a gas compressor and a refrigeration facility which are expensive and troublesome for maintenance. Particularly, when separating chlorine from a gas having a relatively low chlorine concentration, Operation at very high pressure or cryogenic temperature increases equipment costs. In the latter method, carbon tetrachloride is usually used as a solvent. However, the use of carbon tetrachloride has been banned due to environmental problems due to the recent chlorofluorocarbon gas, and cannot be said to be an effective method in the future.

【0004】[0004]

【発明が解決しようとする課題】塩素を含有するガスよ
り塩素を分離する方法の一つに圧力スイング吸着法(以
下、PSA法と略する)がある。しかし、この分離法に
は次のような問題点がある。 (1)吸着塔が塩素で平衡吸着状態に達する前にガス供
給を停止するため、吸着塔上部の吸着剤の一部は未使用
のままである。 (2)吸着塔が塩素で平衡吸着状態に達する前にガス供
給を停止するため、吸着塔上部の塩素未吸着の吸着剤に
他成分のガスが吸着し塩素濃度が低下する。 (3)吸着塔出口側からわずかではあるが塩素がもれ
る。 本発明の目的は上記の問題点がなく、塩素を含有するガ
スより塩素を効率的に分離し濃縮する方法を提供するこ
とにある。
One of the methods for separating chlorine from a chlorine-containing gas is a pressure swing adsorption method (hereinafter abbreviated as PSA method). However, this separation method has the following problems. (1) Since the gas supply is stopped before the adsorption tower reaches the equilibrium adsorption state with chlorine, a part of the adsorbent on the upper part of the adsorption tower remains unused. (2) Since the gas supply is stopped before the adsorption tower reaches the equilibrium adsorption state with chlorine, another component gas is adsorbed by the non-adsorbed adsorbent in the upper part of the adsorption tower, and the chlorine concentration decreases. (3) Chlorine leaks slightly from the outlet side of the adsorption tower. An object of the present invention is to provide a method for efficiently separating and concentrating chlorine from a gas containing chlorine without the above problems.

【0005】[0005]

【課題を解決するための手段】本発明者らは、前記の問
題点を有しない塩素ガスの濃縮方法について鋭意検討
し、塩素を吸着しうる吸着剤を充填した吸着塔をカスケ
ード連結し、塩素を含有する原料ガスを第1吸着塔が塩
素で平衡吸着状態に達するまで導入して塩素を吸着さ
せ、その間第2吸着塔は第1吸着塔出側口から流出する
塩素を僅かに含有するガス中の塩素を吸着することによ
り、吸着工程の吸着塔から塩素をもらさずに吸着させ、
その後脱着することにより高濃度の塩素濃縮が可能であ
ることを見出し、本発明に至った。
Means for Solving the Problems The present inventors have intensively studied a method for concentrating chlorine gas which does not have the above-mentioned problems, and cascade-connected an adsorption tower filled with an adsorbent capable of adsorbing chlorine to form a chlorine gas. Is introduced until the first adsorption tower reaches the equilibrium adsorption state with chlorine to adsorb the chlorine, while the second adsorption tower is a gas containing a small amount of chlorine flowing out from the outlet of the first adsorption tower. By adsorbing the chlorine inside, it is adsorbed without getting chlorine from the adsorption tower in the adsorption process,
After desorption, it was found that a high concentration of chlorine could be concentrated, and the present invention was achieved.

【0006】すなわち、本発明は塩素を吸着しうる吸着
剤を充填した吸着塔をカスケード連結し、塩素を含有す
る原料ガスを第1吸着塔が塩素で平衡吸着状態に達する
まで導入して塩素を吸着させ、その間第2吸着塔は第1
吸着塔出口側から流出する塩素を僅かに含有するガス中
の塩素を吸着することにより、吸着工程の吸着塔から塩
素をもらさずに吸着し第1吸着塔が塩素で平衡吸着状
態に達した後ガスの導入を停止し、ガス導入時よりも低
い圧力で脱着を行い、導入ガスの塩素濃度より高い塩素
濃度のガスを得るとともに吸着剤を再生することを特徴
とする塩素ガスの濃縮方法である。
That is, according to the present invention , an adsorption tower filled with an adsorbent capable of adsorbing chlorine is connected in cascade, and a chlorine-containing raw material gas is introduced until the first adsorption tower reaches an equilibrium adsorption state with chlorine. Adsorption, during which the second adsorption tower
By adsorbing chlorine in the gas containing a small amount of chlorine flowing out from the outlet of the adsorption tower, it was adsorbed without receiving chlorine from the adsorption tower in the adsorption step , and the first adsorption tower reached an equilibrium adsorption state with chlorine. After the introduction of gas is stopped, desorption is performed at a pressure lower than that at the time of gas introduction, a gas having a chlorine concentration higher than the chlorine concentration of the introduced gas is obtained, and the adsorbent is regenerated, and the chlorine gas concentrating method is characterized in that is there.

【0007】本発明の方法が適用される塩素を含有する
ガスには塩素以外のガスとして、酸素・窒素・二酸化炭
素・一酸化炭素・水素・アルゴン・メタンなどの炭化水
素等が存在してよいが、圧力スイング吸着法でこれらを
含むガスから塩素を分離するには、これらのガスと吸着
剤との吸着親和力が塩素に対する場合より充分に差があ
るものを選択する必要がある。
The chlorine-containing gas to which the method of the present invention is applied may include oxygen, nitrogen, carbon dioxide, carbon monoxide, hydrogen, hydrocarbons such as argon and methane as gases other than chlorine. However, in order to separate chlorine from gases containing them by the pressure swing adsorption method, it is necessary to select one having a sufficiently different adsorption affinity between these gases and the adsorbent as compared with chlorine.

【0008】そこで本発明の方法に使用する塩素の吸着
剤としては、合成および天然ゼオライト、非ゼオライト
系多孔質酸性酸化物や活性炭および分子ふるいカーボン
のような炭素質吸着剤が選択される。たとえばゼオライ
トとしてはA型、X型、Y型、L型、ZSM型、天然モ
ルデナイトなどが挙げられるが、好ましくはX型、Y
型、L型、ZSM型であり、特に好ましくは高ケイ素含
有のゼオライトである。非ゼオライト系多孔質酸性酸化
物としては、アルミナ、シリカ、シリカアルミナ、チタ
ニア、マグネシア等があげられる。活性炭としては果実
殻活性炭が好ましい。
Accordingly, as the chlorine adsorbent used in the method of the present invention, a carbonaceous adsorbent such as synthetic and natural zeolites, non-zeolitic porous acidic oxides, activated carbon and molecular sieve carbon is selected. For example, the zeolite includes A-type, X-type, Y-type, L-type, ZSM-type, natural mordenite, etc., and preferably X-type, Y-type
Type, L type and ZSM type, and particularly preferably a zeolite containing high silicon. Examples of the non-zeolitic porous acidic oxide include alumina, silica, silica alumina, titania, magnesia and the like. As the activated carbon, fruit shell activated carbon is preferred.

【0009】これらの吸着剤に対しては、塩素は前記の
ガスに比較しより強い親和力を有しているので、これら
の吸着剤を充填した吸着塔に塩素を含有するガスを導入
すると塩素が他のガスよりも優先的に吸着されるので、
吸着塔のガス出口側では塩素濃度の低いガスが、時には
ほとんど検出されない程度までのガスが得られる。
[0009] Since chlorine has a stronger affinity for these adsorbents than the above-mentioned gases, when chlorine-containing gas is introduced into an adsorption tower filled with these adsorbents, chlorine is reduced. Because it is adsorbed preferentially over other gases,
At the gas outlet side of the adsorption tower, a gas having a low chlorine concentration is obtained to such an extent that it is sometimes hardly detected.

【0010】本発明の方法では以下の点でPSA法の欠
点をカバーしている。従来のPSA法による塩素濃縮で
は、吸着塔への塩素の吸着が進み、平衡吸着状態になる
前に塩素を含有する原料ガスの吸着塔への供給を停止す
る。これは吸着塔に塩素が平衡吸着状態に近ずくまで原
料ガスを供給すると吸着塔出口側から塩素が破過してし
まい、この時に破過する塩素を回収するための除去塔等
の設備が新たに必要となるためである。平衡吸着状態前
に原料ガスの供給を停止した吸着塔内には塩素が吸着し
ていないボイド部が生じ、この部分に他のガスが残留す
る。従って再生時に得られる塩素はこの残留ガスのため
十分な濃度にはならない。
The method of the present invention covers the disadvantages of the PSA method in the following points. In the conventional chlorine concentration by the PSA method, the adsorption of chlorine to the adsorption tower progresses, and the supply of the chlorine-containing raw material gas to the adsorption tower is stopped before the equilibrium adsorption state is established. This is because if the raw material gas is supplied to the adsorption tower until it approaches the equilibrium adsorption state, the chlorine will break through from the outlet side of the adsorption tower, and equipment such as a removal tower to collect the chlorine that breaks down at this time will be newly installed. This is because it is necessary. In the adsorption tower where the supply of the raw material gas is stopped before the equilibrium adsorption state, a void portion in which chlorine is not adsorbed is generated, and other gas remains in this portion. Therefore, chlorine obtained at the time of regeneration does not become a sufficient concentration due to the residual gas.

【0011】これに対し本発明の方法では、吸着塔をカ
スケード連結し、第1吸着塔が平衡状態になるまで塩素
を吸着させることにより、その間に破過した塩素は第2
吸着塔で吸着させる。このため吸着工程の系外に塩素が
もれる心配がない。さらに第1吸着塔では塩素で平衡吸
着状態になるまで原料ガスを供給するため、吸着塔内に
ボイド部がなくなり塩素以外のガスの残留はわずかとな
り再生時に得られる塩素は高濃度のものとなる。また平
衡吸着を行うことにより、吸着剤の未吸着部分がなくな
り吸着剤を有効に利用できる。
On the other hand, in the method of the present invention, the adsorption towers are connected in cascade, and chlorine is adsorbed until the first adsorption tower is in an equilibrium state.
Adsorb in the adsorption tower. Therefore, there is no fear that chlorine leaks out of the system in the adsorption step. Further, in the first adsorption tower, since the raw material gas is supplied until the state of equilibrium adsorption with chlorine is reached, voids are eliminated in the adsorption tower, and the amount of gas other than chlorine remains small, and the chlorine obtained during regeneration has a high concentration. . By performing equilibrium adsorption, the unadsorbed portion of the adsorbent is eliminated, and the adsorbent can be used effectively.

【0012】本発明方法の特徴は、平衡吸着状態を利用
した圧力スイング吸着法であるが、ここで述べる平衡吸
着状態とは、吸着剤へのガス吸着が進み平衡濃度に到達
後には吸着量の増加はなく吸着量は一定となる状態のこ
とであり、ある吸着温度および圧力条件下での平衡吸着
量は吸着剤により一定である(図1参照)。
A feature of the method of the present invention is a pressure swing adsorption method utilizing an equilibrium adsorption state. The term "equilibrium adsorption state" as used herein means that the gas adsorption to the adsorbent progresses and the adsorbed amount is reached after reaching the equilibrium concentration. This is a state in which the amount of adsorption is constant without increasing, and the amount of equilibrium adsorption under a certain adsorption temperature and pressure condition is constant depending on the adsorbent (see FIG. 1).

【0013】吸着剤に吸着させる塩素を含有するガスの
塩素濃度には特に制限はないが、通常5〜80%塩素濃
度が適用される。塩素濃度が低い場合には脱着による再
生操作までの吸着時間は長く取ることができる。なおこ
の吸着操作の操作圧力は後の塩素の脱着操作より高い圧
力にする。操作温度は充填するゼオライトの種類・導入
ガスに含まれる塩素以外のガスの種類や経済的な問題で
決定される。たとえばY型ゼオライトを吸着剤として使
用し、同伴ガスに二酸化炭素が混合されている場合には
常温付近でも充分な塩素吸着を行うことができる。一
方、充填物の劣化防止や設備の材質劣化を防止するため
に原料ガス中の水分は低い方が良く、1000ppm以
下が望ましい。
The chlorine concentration of the gas containing chlorine to be adsorbed by the adsorbent is not particularly limited, but usually a chlorine concentration of 5 to 80% is applied. When the chlorine concentration is low, the adsorption time until the regeneration operation by desorption can be long. The operation pressure of this adsorption operation is set to be higher than that of the subsequent chlorine desorption operation. The operating temperature is determined by the type of zeolite to be filled, the type of gas other than chlorine contained in the introduced gas, and economical problems. For example, when Y-type zeolite is used as an adsorbent and carbon dioxide is mixed in the accompanying gas, sufficient chlorine adsorption can be performed even at around normal temperature. On the other hand, in order to prevent the deterioration of the packing material and the material of the equipment, the moisture in the raw material gas is preferably low, and is preferably 1000 ppm or less.

【0014】吸着工程は第1吸着塔および第2吸着塔の
2塔で行われる。第1吸着塔への塩素の吸着が進み、平
衡吸着状態に達したところで原料ガスとしての塩素を含
有するガスの吸着塔への供給を停止する。この間第2吸
着塔は第1吸着塔出口側から流出する塩素を僅かに含有
するガス中の塩素を吸着することにより、吸着工程から
塩素をもらさずに吸着分離を行うことができる。 続い
て第1吸着塔の操作圧力を降下させ、吸着している塩素
およびその他のガスを脱着させる。この時の操作圧力は
吸着時の圧力以下とし、必要に応じて真空ポンプにより
大気圧以下にすることも有効である。 塩素を僅かに吸
着した第2吸着塔には引き続き原料ガスを導入し、塩素
で平衡吸着状態に達したところで供給を停止する。この
間昇圧工程を終了した第3吸着塔は第2吸着塔出口側か
ら流出する塩素を僅かに含有するガス中の塩素を吸着す
る。操作温度は任意であるが、基本的には吸着時の温度
と同じとする方が経済的である。もちろん経済的に有効
であればいわゆるサーマルスイング方式をとることも可
能である。
The adsorption step is performed in two columns, a first adsorption column and a second adsorption column. When the adsorption of chlorine to the first adsorption tower progresses and reaches an equilibrium adsorption state, the supply of the gas containing chlorine as a raw material gas to the adsorption tower is stopped. During this time, the second adsorption tower adsorbs chlorine in the gas containing a small amount of chlorine flowing out from the outlet side of the first adsorption tower, so that the adsorption and separation can be performed without receiving chlorine from the adsorption step. Subsequently, the operating pressure of the first adsorption tower is lowered to desorb the adsorbed chlorine and other gases. At this time, the operation pressure is set to be equal to or lower than the pressure at the time of adsorption, and if necessary, it is also effective to set the pressure to equal to or lower than the atmospheric pressure by using a vacuum pump. The raw material gas is continuously introduced into the second adsorption tower that has slightly adsorbed chlorine, and the supply is stopped when the equilibrium adsorption state is reached with chlorine. During this period, the third adsorption tower, which has completed the pressure raising step, adsorbs the chlorine in the gas containing a small amount of chlorine flowing out from the outlet side of the second adsorption tower. The operating temperature is optional, but it is basically more economical to set the temperature at the time of adsorption. Of course, if economically effective, a so-called thermal swing method can be used.

【0015】更に脱着操作時に少量の不活性ガス、好ま
しくは窒素ガスを通気させることは吸着剤から塩素ガス
の脱着が促進され好ましい態様である。この脱着操作に
より導入ガスよりも塩素濃度の高いガスを得ることがで
きるとともに、塩素を吸着した吸着剤を脱塩素すること
で再生することができ、再び次の吸着操作を行うことが
できる。
Further, it is a preferable embodiment that a small amount of an inert gas, preferably nitrogen gas, is passed during the desorption operation because the desorption of chlorine gas from the adsorbent is promoted. By this desorption operation, a gas having a higher chlorine concentration than the introduced gas can be obtained, and the adsorbent that has adsorbed chlorine can be regenerated by dechlorination, and the next adsorption operation can be performed again.

【0016】次に、工業規模におけるより具体的な形で
の実施の状態について説明する。図2はその形態を示
す。
Next, the state of implementation in a more specific form on an industrial scale will be described. FIG. 2 shows the form.

【0017】図2では、塩素を含有する原料ガスは管1
よりガス圧縮機2に送られ、ここで所定吸着圧力まで昇
圧された後、切換弁3を経て、4基の吸着塔4a、4
b、4c、4dの内の第1の吸着塔4aに送り込まれ
る。4基の吸着塔4a、4b、4c、4dは各々前出の
塩素を優先的に吸着する吸着剤が充填されており、加圧
状態で導入された原料ガス中の塩素が優先的に吸着さ
れ、吸着塔4aの出口には塩素の含有率の低いガス、時
にはほとんど検出できない程度に低い塩素濃度のガス
(以下処理済ガスとする)が得られる。この処理済ガス
は切換弁25、26を経て第2吸着塔4bに送られ、処
理済ガス中の塩素を吸着して検出できない程度に低い塩
素濃度のガス(以下排ガスとする)が得られる。この排
ガスは切換弁15、弁6を経てブロア7に送られ、排出
される(吸着工程)。
In FIG. 2, the raw material gas containing chlorine is a pipe 1
After being sent to the gas compressor 2 where the pressure is increased to a predetermined adsorption pressure, the gas is passed through the switching valve 3 to the four adsorption towers 4 a and 4.
b, 4c and 4d are sent to the first adsorption tower 4a. Each of the four adsorption towers 4a, 4b, 4c, and 4d is filled with an adsorbent that preferentially adsorbs the above-mentioned chlorine, and preferentially adsorbs chlorine in the source gas introduced in a pressurized state. At the outlet of the adsorption tower 4a, a gas having a low chlorine content, and sometimes a gas having a chlorine concentration low enough to be hardly detectable (hereinafter referred to as a treated gas) is obtained. The treated gas is sent to the second adsorption tower 4b via the switching valves 25 and 26, and a gas having a chlorine concentration low enough to detect and detect the chlorine in the treated gas (hereinafter referred to as exhaust gas) is obtained. This exhaust gas is sent to the blower 7 via the switching valve 15 and the valve 6, and is discharged (adsorption step).

【0018】この時、第3吸着塔4cでは、第2吸着塔
4bから吐出した排ガスの一部が流量調節機構8、切換
弁16を経て第3の吸着塔4c内に導入され、この塔内
の圧力が排ガスによって高められる充圧工程が実施され
ており、また第4の吸着塔4dではこの塔内と真空ポン
プ10とが切換弁23、12aを経て接続され、この塔
内の吸着剤が減圧状態で再生処理される再生工程が実施
されている。そして所定量の塩素を吸着して平衡吸着状
態に達した吸着塔4aは、切換弁3の切り換えによって
原料ガスの導入が停止されると共に、切換弁13の切り
換えによって塔内が真空ポンプ10で排気されて減圧状
態になり、吸着剤に吸着された塩素が脱着され、吸着剤
が再生される(再生工程)。この再生工程で製品として
の塩素濃度の高いガスを真空ポンプ10の吐出口から得
ることができ、この塩素を高濃度に含有したガスは下流
の消費工程に送られる。
At this time, in the third adsorption tower 4c, a part of the exhaust gas discharged from the second adsorption tower 4b is introduced into the third adsorption tower 4c via the flow rate control mechanism 8 and the switching valve 16, and this column In the fourth adsorption tower 4d, the inside of the fourth adsorption tower 4d and the vacuum pump 10 are connected via the switching valves 23 and 12a, and the adsorbent in this tower is A regeneration step of performing a regeneration process under reduced pressure is performed. The adsorption tower 4a that has reached the equilibrium adsorption state by adsorbing a predetermined amount of chlorine stops the introduction of the raw material gas by switching the switching valve 3 and exhausts the inside of the tower by the vacuum pump 10 by switching the switching valve 13. Then, the pressure is reduced, the chlorine adsorbed on the adsorbent is desorbed, and the adsorbent is regenerated (regeneration step). In this regeneration step, a gas having a high chlorine concentration as a product can be obtained from the discharge port of the vacuum pump 10, and the gas containing a high concentration of chlorine is sent to a downstream consumption step.

【0019】この時第2吸着塔4bでは、吸着塔4aか
らの処理済ガスの導入終了後原料ガスが切換弁14を経
て導入され、この塔の出口から処理済ガスが得られる。
この処理済ガスは切換弁27、28を経て第3吸着塔4
cに送られ、処理済ガス中の塩素が吸着され、吸着塔4
cの出口側には検出できない程度の低い塩素濃度の排ガ
スが得られる。この排ガスは切換弁18、弁6を経てブ
ロア7に送られ、排出される。また第4の吸着塔4dで
は第3の吸着塔4cから吐出される排ガスの一部が流量
調節機構8、切換弁23を経て導入され、この塔内の圧
力が排ガスによって高められる充圧工程が実施されてい
る。
At this time, in the second adsorption tower 4b, after the introduction of the treated gas from the adsorption tower 4a is completed, the raw material gas is introduced via the switching valve 14, and the treated gas is obtained from the outlet of this tower.
The treated gas passes through the switching valves 27 and 28 and passes through the third adsorption tower 4
c, the chlorine in the treated gas is adsorbed,
Exhaust gas having a chlorine concentration low enough to be undetectable is obtained at the outlet side of c. This exhaust gas is sent to the blower 7 via the switching valve 18 and the valve 6, and is discharged. In the fourth adsorption tower 4d, a part of the exhaust gas discharged from the third adsorption tower 4c is introduced through the flow rate control mechanism 8 and the switching valve 23, and the pressure in the column is increased by the exhaust gas. It has been implemented.

【0020】その後第3の吸着塔4cでは、吸着塔4b
からの処理済ガスの導入終了後原料ガスが切換弁17を
経て導入され、この塔の出口から処理済ガスが得られ
る。この処理済ガスは切換弁29、30を経て第4吸着
塔4dに送られ、処理済ガス中の塩素が吸着され、吸着
塔4dの出側には検出できない程度に低い塩素濃度の排
ガスが得られる。この排ガスは切換弁24、弁6を経て
ブロア7に送られ、排出される。また第1の吸着塔4a
では第4の吸着塔4dから吐出される排ガスの一部が流
量調節機構8、切換弁19を経て導入され、この塔内の
圧力が排ガスによって高められる充圧工程が実施されて
いる。
Thereafter, in the third adsorption tower 4c, the adsorption tower 4b
After the introduction of the treated gas from the column, the raw material gas is introduced through the switching valve 17, and the treated gas is obtained from the outlet of this column. This treated gas is sent to the fourth adsorption tower 4d via the switching valves 29 and 30, and the chlorine in the treated gas is adsorbed, and an exhaust gas having a chlorine concentration low enough to be undetectable is obtained at the outlet side of the adsorption tower 4d. Can be This exhaust gas is sent to the blower 7 via the switching valve 24 and the valve 6, and is discharged. Also, the first adsorption tower 4a
In the method, a part of the exhaust gas discharged from the fourth adsorption tower 4d is introduced through the flow rate adjusting mechanism 8 and the switching valve 19, and a pressure step of increasing the pressure in the tower by the exhaust gas is performed.

【0021】原料ガス中の塩素を吸着して平衡吸着状態
に達した吸着塔4bは、切換弁14の切り換えによって
原料ガスの導入が停止されると共に、切換弁20の切り
換えによって塔内の真空ポンプ10で排気されて減圧状
態になり、吸着剤に吸着された塩素が脱着され、吸着剤
が再生される。
In the adsorption tower 4b which has reached the equilibrium adsorption state by adsorbing chlorine in the raw material gas, the introduction of the raw material gas is stopped by switching the switching valve 14, and the vacuum pump in the tower is switched by switching the switching valve 20. The gas is exhausted at 10 to be in a reduced pressure state, the chlorine adsorbed by the adsorbent is desorbed, and the adsorbent is regenerated.

【0022】以下同様に、この一連操作を4基の吸着塔
4a、4b、4c、4dについて交互に操り返すことに
よって塩素を含有する原料ガスより塩素を分離し、原料
ガス中の塩素濃度以上の塩素濃度のガスを連続的に得る
ことができる。
Similarly, by repeating this series of operations alternately for the four adsorption towers 4a, 4b, 4c, and 4d, chlorine is separated from the chlorine-containing raw material gas, and the chlorine concentration in the raw material gas is increased. A gas having a chlorine concentration can be continuously obtained.

【0023】[0023]

【実施例】次に、実施例により本発明をさらに詳細に説
明する。 実施例1 合成Y型ゼオライト(ZEOCHEM製)を夫々20g
充填したステンレス製の吸着塔4塔中の第1吸着塔に2
5〜30℃にて塩素(5%)・二酸化炭素(15%)・
ヘリウム(80%)の組成の原料ガスを5atmの圧力
に調節して200ml/minで、第1吸着塔出側の処
理済ガスの組成が原料ガスと同成分になるまで34分間
通気した。この間の処理済ガスは第2吸着塔に通気され
るが、第2吸着塔出側の排ガスをガスクロマトグラフ分
析を行いガス組成を分析したところ、塩素ガスは不検出
であった。通気完了後、第1吸着塔への原料ガスの供給
を停止し、真空ポンプで吸着塔を60mmHg ab
s.の圧力に5分間おき、塩素ガスを脱着させた。脱着
したガスを分析したところ塩素濃度86%であった。第
1吸着塔からの処理済ガスの通気を完了した第2吸着塔
に引続き原料ガスを通気して第2吸着塔出側の処理済ガ
スの組成が原料ガスと同成分になるまで20分間通気し
た。この間の処理済ガスは第3吸着塔に通気されるが、
第3吸着塔出側の排ガスをガスクロマトグラフ分析を行
いガス組成を分析したところ塩素ガスは不検出であっ
た。通気完了後、第2吸着塔への原料ガスの供給を停止
し、真空ポンプで吸着塔を60mmHg abs.の圧
力に5分間おき、塩素ガスを脱着させた。脱着したガス
を分析したところ塩素濃度86%であった。
Next, the present invention will be described in more detail with reference to examples. Example 1 20 g each of synthetic Y-type zeolite (manufactured by ZEOCHEM)
The first of the four packed stainless steel adsorption towers
Chlorine (5%), carbon dioxide (15%) at 5-30 ° C
A source gas having a composition of helium (80%) was adjusted to a pressure of 5 atm and aerated at 200 ml / min for 34 minutes until the composition of the treated gas on the exit side of the first adsorption tower became the same as that of the source gas. During this time, the treated gas is passed through the second adsorption tower, and the exhaust gas on the outlet side of the second adsorption tower was subjected to gas chromatographic analysis to analyze the gas composition. As a result, no chlorine gas was detected. After the completion of the aeration, the supply of the raw material gas to the first adsorption tower was stopped, and the adsorption tower was moved to 60 mmHg ab by a vacuum pump.
s. At a pressure of 5 minutes to desorb chlorine gas. Analysis of the desorbed gas revealed a chlorine concentration of 86%. After passing the treated gas from the first adsorption tower through the second adsorption tower, the raw material gas is continuously passed through the second adsorption tower, and the treated gas at the outlet side of the second adsorption tower is passed for 20 minutes until the composition of the treated gas becomes the same as the source gas. did. During this time, the treated gas is passed through the third adsorption tower,
Gas chromatographic analysis of the exhaust gas on the exit side of the third adsorption tower was performed to analyze the gas composition, and no chlorine gas was detected. After the completion of the ventilation, the supply of the raw material gas to the second adsorption tower was stopped, and the adsorption tower was evacuated to 60 mmHg abs. At a pressure of 5 minutes to desorb chlorine gas. Analysis of the desorbed gas revealed a chlorine concentration of 86%.

【0024】実施例2 合成13X型ゼオライト(富士デビソン製)を夫々20
g充填したステンレス製の吸着塔4塔中の第1吸着塔に
60℃にて塩素(5%)・二酸化炭素(15%)・ヘリ
ウム(80%)の組成の原料ガスを5atmの圧力に調
節して200ml/minで、第1吸着塔出側の処理済
ガスの組成が原料ガスと同成分になるまで17分間通気
した。この間の処理済ガスは第2吸着塔に通気される
が、第2吸着塔出側の排ガスをガスクロマトグラフ分析
を行いガス組成を分析したところ、塩素ガスは不検出で
あった。通気完了後、第1吸着塔への原料ガスの供給を
停止し、真空ポンプで吸着塔を60mmHg abs.
の圧力に5分間おき、塩素ガスを脱着させた。脱着した
ガスを分析したところ塩素濃度80%であった。第1吸
着塔からの処理済ガスの通気を完了した第2吸着塔に引
続き原料ガスを通気して第2吸着塔出側の処理済ガスの
組成が原料ガスと同成分になるまで10分間通気した。
この間の処理済ガスは第3吸着塔に通気されるが、第3
吸着塔出側の排ガスをガスクロマトマトグラフ分析を行
いガス組成を分析したところ、塩素ガスは不検出であっ
た。通気完了後、第2吸着塔への原料ガスの供給を停止
し、真空ポンプで吸着塔を60mmHg abs.の圧
力に5分間おき、塩素ガスを脱着させた。脱着したガス
を分析したところ、塩素濃度は80%であった。
Example 2 Synthetic 13X type zeolite (manufactured by Fuji Devison) was used for 20 samples each.
The raw material gas having a composition of chlorine (5%), carbon dioxide (15%) and helium (80%) is adjusted to a pressure of 5 atm at 60 ° C. in the first adsorption tower among the four stainless steel adsorption towers filled with g. Then, air was passed at 200 ml / min for 17 minutes until the composition of the treated gas on the exit side of the first adsorption tower became the same as that of the raw material gas. During this time, the treated gas is passed through the second adsorption tower, and the exhaust gas on the outlet side of the second adsorption tower was subjected to gas chromatographic analysis to analyze the gas composition. As a result, no chlorine gas was detected. After the completion of the ventilation, the supply of the raw material gas to the first adsorption tower was stopped, and the adsorption tower was operated at 60 mmHg abs.
At a pressure of 5 minutes to desorb chlorine gas. Analysis of the desorbed gas revealed a chlorine concentration of 80%. After passing the treated gas from the first adsorption tower through the second adsorption tower, the source gas is continuously passed through the second adsorption tower, and the composition of the treated gas on the exit side of the second adsorption tower becomes the same as the source gas for 10 minutes. did.
During this time, the treated gas is passed through the third adsorption tower.
Gas chromatograph analysis of the exhaust gas on the exit side of the adsorption tower was performed to analyze the gas composition, and no chlorine gas was detected. After the completion of the ventilation, the supply of the raw material gas to the second adsorption tower was stopped, and the adsorption tower was evacuated to 60 mmHg abs. At a pressure of 5 minutes to desorb chlorine gas. When the desorbed gas was analyzed, the chlorine concentration was 80%.

【0025】実施例3 ガス吸着活性炭PCB(東洋アルゴン製)を夫々10g
充填したステンレス製の吸着塔4塔中の第1吸着塔に6
0℃にて塩素(5%)・二酸化炭素(15%)・ヘリウ
ム(80%)の組成の原料ガスを5atmの圧力に調節
して200ml/minで、第1吸着塔出側の処理済ガ
スの組成が原料ガスと同成分になるまで17分間通気し
た。この間の吸着済ガスは第2吸着塔に通気されるが、
第2吸着塔出側の排ガスをガスクロマトグラフ分析を行
いガス組成を分析したところ、塩素ガスは不検出であっ
た。通気完了後、第1吸着塔への原料ガスの供給を停止
し、真空ポンプで吸着塔を60mmHg abs.の圧
力に5分間おき、塩素ガスを脱着させた。脱着したガス
を分析したところ、塩素濃度80%であった。第1吸着
塔からの処理済ガスの通気を完了した第2吸着塔に引続
き原料ガスを通気して、第2吸着塔出側の処理済ガスの
組成が原料ガスと同成分になるまで10分間通気した。
この間処理済みガスは第3吸着塔に通気されるが、第3
吸着塔出側の排ガスをガスクロマトグラフ分析を行いガ
ス組成を分析したところ、塩素ガスは不検出であった。
通気完了後、第2吸着塔への原料ガスの供給を停止し、
真空ポンプで吸着塔を60mmHg abs.の圧力に
5分間おき、塩素ガスを脱着させた。脱着したガスを分
析したところ塩素濃度80%であった。
Example 3 10 g each of gas-adsorbed activated carbon PCB (manufactured by Toyo Argon)
In the first of four packed stainless steel adsorption towers, 6
A raw gas having a composition of chlorine (5%), carbon dioxide (15%) and helium (80%) is adjusted to a pressure of 5 atm at 0 ° C., and the treated gas on the exit side of the first adsorption tower is adjusted at 200 ml / min. Until the composition became the same as that of the source gas. During this time, the adsorbed gas is passed through the second adsorption tower,
Gas chromatographic analysis of the exhaust gas on the exit side of the second adsorption tower was performed to analyze the gas composition, and no chlorine gas was detected. After the completion of the ventilation, the supply of the raw material gas to the first adsorption tower was stopped, and the adsorption tower was operated at 60 mmHg abs. At a pressure of 5 minutes to desorb chlorine gas. When the desorbed gas was analyzed, the chlorine concentration was 80%. After passing the treated gas from the first adsorption tower through the second adsorption tower which has been completely ventilated, the source gas is passed continuously, and the composition of the treated gas on the exit side of the second adsorption tower becomes the same as the source gas for 10 minutes. Ventilated.
During this time, the treated gas is passed through the third adsorption tower.
Gas chromatographic analysis of the exhaust gas on the exit side of the adsorption tower was performed to analyze the gas composition, and no chlorine gas was detected.
After the completion of the aeration, the supply of the raw material gas to the second adsorption tower is stopped,
Using a vacuum pump, set the adsorption tower at 60 mmHg abs. At a pressure of 5 minutes to desorb chlorine gas. Analysis of the desorbed gas revealed a chlorine concentration of 80%.

【0026】実施例4 分子ふるいカーボンMSC(武田薬品製)を夫々10g
充填したステンレス製の吸着塔4塔中の第1吸着塔に6
0℃にて塩素(5%)・二酸化炭素(15%)・ヘリウ
ム(80%)の組成の原料ガスを5atmの圧力に調節
して200ml/minで、第1吸着塔出側の処理済ガ
スの組成が原料ガスと同成分になるまで17分間通気し
た。この間の処理済ガスは第2吸着塔に通気されるが、
第2吸着塔出側の排ガスをガスクロマトグラフ分析を行
いガス組成を分析したところ、塩素ガスは不検出であっ
た。通気完了後、第1吸着塔への原料ガスの供給を停止
し、真空ポンプで吸着塔を60mmHg abs.の圧
力に5分間おき、塩素ガスを脱着させた。脱着したガス
を分析したところ塩素濃度83%であった。第1吸着塔
からの処理済ガスの通気を完了した第2吸着塔に、引続
き原料ガスを通気して第2吸着塔出側の処理済ガスの組
成が原料ガスと同成分になるまで、10分間通気した。
この間の処理済ガスは第3吸着塔に通気されるが、第3
吸着塔出側の排ガスをガスクロマトグラフ分析を行いガ
ス組成の分析をしたところ、塩素ガスは不検出であっ
た。通気完了後、第2吸着塔への原料ガスの供給を停止
し、真空ポンプで吸着塔を60mmHg abs.の圧
力に5分間おき、塩素ガスを脱着させた。脱着したガス
を分析したところ塩素濃度83%であった。
Example 4 10 g each of molecular sieve carbon MSC (manufactured by Takeda Pharmaceutical Co., Ltd.)
In the first of four packed stainless steel adsorption towers, 6
A raw gas having a composition of chlorine (5%), carbon dioxide (15%) and helium (80%) is adjusted to a pressure of 5 atm at 0 ° C., and the treated gas on the exit side of the first adsorption tower is adjusted at 200 ml / min. Until the composition became the same as that of the source gas. During this time, the treated gas is passed through the second adsorption tower,
Gas chromatographic analysis of the exhaust gas on the exit side of the second adsorption tower was performed to analyze the gas composition, and no chlorine gas was detected. After the completion of the ventilation, the supply of the raw material gas to the first adsorption tower was stopped, and the adsorption tower was operated at 60 mmHg abs. At a pressure of 5 minutes to desorb chlorine gas. When the desorbed gas was analyzed, the chlorine concentration was 83%. The raw material gas is continuously passed through the second adsorption tower where the passage of the treated gas from the first adsorption tower is completed, and the composition of the treated gas on the exit side of the second adsorption tower becomes the same as that of the source gas. Aerated for minutes.
During this time, the treated gas is passed through the third adsorption tower.
Gas chromatographic analysis of the exhaust gas on the exit side of the adsorption tower and analysis of the gas composition revealed that chlorine gas was not detected. After the completion of the ventilation, the supply of the raw material gas to the second adsorption tower was stopped, and the adsorption tower was evacuated to 60 mmHg abs. At a pressure of 5 minutes to desorb chlorine gas. When the desorbed gas was analyzed, the chlorine concentration was 83%.

【0027】比較例1 合成Y型ゼオライト(ZEOCHEM製)を夫々20g
充填したステンレス製の吸着塔3塔中の第1吸着塔に2
5〜30℃にて塩素(5%)・二酸化炭素(15%)・
ヘリウム(80%)の組成のガスを5atmの圧力に調
節して200ml/minで、第1吸着塔出側から塩素
が破過する前までの13分間通気した。この間カラムか
ら流出するガスをガスクロマトグラフ分析を行いガス組
成を分析したところ塩素ガスは100〜300ppm検
出された。通気完了後、第1吸着塔への原料ガスの供給
を停止し、真空ポンプで第1吸着塔を60mmHg a
bs.の圧力に5分間おき、塩素ガスを脱着させた。脱
着したガスを分析したところ塩素濃度55%であった。
この脱着後の第1吸着塔に再び初めと同様の組成のガス
を同条件で通気したところ、やはり13分間は流出する
ガスの塩素濃度は100〜300ppmであった。
Comparative Example 1 20 g each of synthetic Y-type zeolites (manufactured by ZEOCHEM)
The first of three packed stainless steel adsorption towers has 2
Chlorine (5%), carbon dioxide (15%) at 5-30 ° C
A gas having a composition of helium (80%) was adjusted to a pressure of 5 atm and aerated at 200 ml / min for 13 minutes from the outlet side of the first adsorption tower until chlorine passed. During this time, the gas flowing out of the column was analyzed by gas chromatography to analyze the gas composition. As a result, 100 to 300 ppm of chlorine gas was detected. After the completion of the aeration, the supply of the raw material gas to the first adsorption tower was stopped, and the first adsorption tower was moved to 60 mmHg a by a vacuum pump.
bs. At a pressure of 5 minutes to desorb chlorine gas. Analysis of the desorbed gas revealed a chlorine concentration of 55%.
When a gas having the same composition as the first gas was again passed through the first adsorption tower after the desorption under the same conditions, the chlorine concentration of the gas flowing out for 13 minutes was 100 to 300 ppm.

【0028】[0028]

【発明の効果】本発明は圧力スイング吸着法を改良する
ことにより、塩素を含有するガスより塩素を系外にもら
さず、かつ高濃度に濃縮し、また吸着剤を有効に利用す
る方法を提供するもので、その工業的価値は非常に大き
い。
The present invention provides a method for improving the pressure swing adsorption method so that chlorine is not taken out of the system from the chlorine-containing gas, is concentrated to a high concentration, and the adsorbent is effectively used. The industrial value is very large.

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

【図1】各吸着剤の吸着曲線グラフである。FIG. 1 is an adsorption curve graph of each adsorbent.

【図2】本発明を特に連続的に行うために複数の吸着塔
を用いる設備の模式図である。
FIG. 2 is a schematic view of an installation using a plurality of adsorption towers for performing the present invention particularly continuously.

【符号の説明】[Explanation of symbols]

1. 原料ガス供給管 2. 圧縮機 4a.4b.4c. 吸着塔 6. 弁 7. ブロア 8. 流量調節機構 10. 真空ポンプ 3,5,9,11,12a,12b,13〜32 切換
1. Source gas supply pipe 2. Compressor 4a. 4b. 4c. Adsorption tower 6. Valve 7. Blower 8. Flow control mechanism 10. Vacuum pump 3,5,9,11,12a, 12b, 13-32 Switching valve

───────────────────────────────────────────────────── フロントページの続き (72)発明者 伊藤 洋之 福岡県大牟田市浅牟田町30 三井東圧化 学株式会社内 (72)発明者 菊地 功 福岡県大牟田市浅牟田町30 三井東圧化 学株式会社内 審査官 鈴木 紀子 (58)調査した分野(Int.Cl.6,DB名) C01B 7/01 C01B 7/07 B01D 53/04 ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Hiroyuki Ito 30 Asamuta-cho, Omuta-shi, Fukuoka Prefecture Inside Mitsui Toatsu Chemicals Co., Ltd. Examiner Noriko Suzuki (58) Field surveyed (Int.Cl. 6 , DB name) C01B 7/01 C01B 7/07 B01D 53/04

Claims (5)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 塩素を吸着しうる吸着剤を充填した吸着
塔をカスケード連結し、塩素を含有する原料ガスを第1
吸着塔が塩素で平衡吸着状態に達するまで導入して塩素
を吸着させ、その間第2吸着塔は第1吸着塔出口側から
流出する塩素を僅かに含有するガス中の塩素を吸着する
ことにより、吸着工程の吸着塔から塩素をもらさずに吸
着し、第1吸着塔が塩素で平衡吸着状態に達した後ガス
の導入を停止し、ガス導入時よりも低い圧力で脱着を行
い、導入ガスの塩素濃度より高い塩素濃度のガスを得る
とともに吸着剤を再生することを特徴とする塩素ガスの
濃縮方法。
1. An adsorption tower filled with an adsorbent capable of adsorbing chlorine is connected in cascade, and a chlorine-containing raw material gas is converted into a first gas.
The adsorption tower introduces chlorine until it reaches an equilibrium adsorption state with chlorine to adsorb chlorine, while the second adsorption tower adsorbs chlorine in the gas containing a small amount of chlorine flowing out from the outlet of the first adsorption tower, Adsorption is performed without obtaining chlorine from the adsorption tower in the adsorption step. After the first adsorption tower reaches an equilibrium adsorption state with chlorine, the introduction of gas is stopped, and desorption is performed at a lower pressure than when introducing the gas. A method for concentrating chlorine gas, comprising obtaining a gas having a chlorine concentration higher than the chlorine concentration and regenerating the adsorbent.
【請求項2】 塩素を吸着しうる吸着剤がゼオライトで
ある請求項1記載の方法。
2. The method according to claim 1, wherein the adsorbent capable of adsorbing chlorine is zeolite.
【請求項3】 塩素を吸着しうる吸着剤が非ゼオライト
系多孔質酸性酸化物である請求項1記載の方法。
3. The method according to claim 1, wherein the adsorbent capable of adsorbing chlorine is a non-zeolitic porous acidic oxide.
【請求項4】 塩素を吸着しうる吸着剤が活性炭である
請求項1記載の方法。
4. The method according to claim 1, wherein the adsorbent capable of adsorbing chlorine is activated carbon.
【請求項5】 活性炭が分子ふるいカーボンである請求
項4記載の方法。
5. The method according to claim 4, wherein the activated carbon is molecular sieve carbon.
JP3141776A 1991-06-13 1991-06-13 How to concentrate chlorine gas Expired - Lifetime JP2909253B2 (en)

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JP2909253B2 true JP2909253B2 (en) 1999-06-23

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