JPH0373326B2 - - Google Patents

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Publication number
JPH0373326B2
JPH0373326B2 JP59252232A JP25223284A JPH0373326B2 JP H0373326 B2 JPH0373326 B2 JP H0373326B2 JP 59252232 A JP59252232 A JP 59252232A JP 25223284 A JP25223284 A JP 25223284A JP H0373326 B2 JPH0373326 B2 JP H0373326B2
Authority
JP
Japan
Prior art keywords
gas
adsorbent
acidic
nitrogen dioxide
packed bed
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
JP59252232A
Other languages
Japanese (ja)
Other versions
JPS61129027A (en
Inventor
Yoshimi Matsumura
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.)
RODOSHO SANGYO IGAKU SOGO KENKYUSHOCHO
Original Assignee
RODOSHO SANGYO IGAKU SOGO KENKYUSHOCHO
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 RODOSHO SANGYO IGAKU SOGO KENKYUSHOCHO filed Critical RODOSHO SANGYO IGAKU SOGO KENKYUSHOCHO
Priority to JP59252232A priority Critical patent/JPS61129027A/en
Publication of JPS61129027A publication Critical patent/JPS61129027A/en
Publication of JPH0373326B2 publication Critical patent/JPH0373326B2/ja
Granted legal-status Critical Current

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Classifications

    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

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  • Treating Waste Gases (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

発明の目的 Purpose of invention

【産業上の利用分野】[Industrial application field]

本発明は、強酸性の二酸化窒素と弱酸性の炭酸
ガスおよび(または)非酸性ガスとの混合ガス中
の二酸化窒素、たとえば空気中に存在する二酸化
窒素を選択的に吸着分離する方法に関する。本発
明はまた、二酸化窒素、炭酸ガスおよび非酸性ガ
スの混合ガス中の二酸化窒素および炭酸ガスを、
選択的に逐次吸着分離する方法に関する。
The present invention relates to a method for selectively adsorbing and separating nitrogen dioxide in a mixed gas of strongly acidic nitrogen dioxide and weakly acidic carbon dioxide and/or non-acidic gas, such as nitrogen dioxide present in air. The present invention also allows nitrogen dioxide and carbon dioxide in a mixed gas of nitrogen dioxide, carbon dioxide and non-acidic gas to be
This invention relates to a method for selectively sequential adsorption separation.

【従来の技術】[Conventional technology]

従来、酸性ガスに対する分離吸着剤としては、
ソーダライム(化学組成CaO・NaOH)、カ性ソ
ーダ、重炭酸ソーダ(NaHCO3)などの強塩基
性吸着剤やゼオライト、活性炭などの多孔性吸着
剤が用いられている。 ところが、強塩基性吸着剤は、強酸性の二酸化
窒素や二酸化硫黄だけでなく、弱酸性の二酸化炭
素を含むすべての酸性ガスを吸着する。したがつ
て、強塩基性吸着剤では、弱酸性ガスと強酸性ガ
スとを分離することができない。そのために、た
とえば硝酸プラントや有機化合物のニトロ化工程
などの排ガス中に含まれる二酸化窒素のみを除
去、分離することが目的の場合でも、共存する二
酸化炭素が同時に吸着されるので、二酸化窒素に
対する吸着量が減少する。また、ソーダライムや
重炭酸ナトリウムで酸性ガスを吸着したのちは、
吸着したガスの脱着による回収と吸着剤の再生は
困難なので、それを行なわずに、吸着剤はそのま
ま廃棄するか、多の用途に向けるしかない。この
ように、強酸性ガスの吸着分離剤として強塩基性
吸着剤を用いると、その使用効率が低く、また、
吸着したガスの回収による再利用の可能性が乏し
いという問題があつた。 一方、ゼオライトなどの多孔性吸着剤では、酸
性ガスに対する吸着剤単位重量当りの吸着容量が
塩基性吸着剤より小さい。また、これらの吸着剤
は、ガスを非特異的な物理吸着の機構で吸着する
ために、その細孔構造の中に凝縮することのでき
るガスはすべて吸着してしまう。そのために、多
孔性吸着剤では酸性ガスのみを選択的に吸着する
ことができず、加熱により脱着しても複数のガス
が共存する混合ガスとなるので、有効な利用が困
難であるといつた問題があつた。
Conventionally, as a separation adsorbent for acidic gas,
Strongly basic adsorbents such as soda lime (chemical composition: CaO/NaOH), caustic soda, and bicarbonate of soda (NaHCO 3 ), and porous adsorbents such as zeolite and activated carbon are used. However, strongly basic adsorbents adsorb not only strongly acidic nitrogen dioxide and sulfur dioxide, but also all acidic gases including weakly acidic carbon dioxide. Therefore, a strongly basic adsorbent cannot separate weakly acidic gas and strongly acidic gas. For this reason, even if the purpose is to remove and separate only nitrogen dioxide contained in the exhaust gas from a nitric acid plant or the nitration process of organic compounds, the adsorption of nitrogen dioxide quantity decreases. In addition, after adsorbing acid gas with soda lime or sodium bicarbonate,
Since it is difficult to recover the adsorbed gas by desorption and regenerate the adsorbent, the only option is to dispose of the adsorbent as it is or to use it for various purposes. In this way, when a strong basic adsorbent is used as an adsorption/separation agent for strongly acidic gases, its usage efficiency is low, and
There was a problem that there was little possibility of reusing the adsorbed gas by recovering it. On the other hand, porous adsorbents such as zeolites have a smaller adsorption capacity per unit weight of acidic gas than basic adsorbents. Furthermore, since these adsorbents adsorb gases by a non-specific physical adsorption mechanism, all gases that can be condensed into their pore structures are adsorbed. For this reason, porous adsorbents cannot selectively adsorb only acidic gases, and even when desorbed by heating, a mixture of multiple gases coexists, making it difficult to use them effectively. There was a problem.

【解決しようとする問題点】[Problems to be solved]

本発明のひとつの目的は、上記の問題点を解決
し、強酸性ガスである二酸化窒素と、弱酸性ガス
および(または)非酸性ガスとの混合ガスから二
酸化窒素を選択的に分離することができ、また、
吸着分離したガスの脱着回収および吸着剤の再利
用が容易な吸着分離法を提供することにある。 本発明のいまひとつの目的は、二酸化窒素、炭
酸ガスおよび非酸性ガスの混合ガス中の二酸化窒
素および炭酸ガスを、選択的に逐次吸着分離する
方法を提供することにある。 発明の構成
One object of the present invention is to solve the above problems and to selectively separate nitrogen dioxide from a mixed gas of strongly acidic nitrogen dioxide and weakly acidic gas and/or non-acidic gas. I can do it, and also.
An object of the present invention is to provide an adsorption separation method that allows easy desorption recovery of adsorbed and separated gases and reuse of adsorbents. Another object of the present invention is to provide a method for selectively and sequentially adsorbing and separating nitrogen dioxide and carbon dioxide in a mixed gas of nitrogen dioxide, carbon dioxide, and non-acidic gas. Composition of the invention

【問題点を解決するための手段】 一般に、塩基吸着剤は酸性ガスを吸着するが、
発明者は、塩基性吸着性剤の中でも塩基性強度の
弱い吸着剤、とくに酸化マグネシウム、酸化亜鉛
および酸化ベリリウムが、強酸性の二酸化窒素は
吸着するが弱酸性の炭酸ガスは吸着しないことを
見出した。 上記のような知見に基づいて完成された本発明
は、その基本的な態様として、強酸性ガスである
二酸化窒素と、弱酸性ガスである炭酸ガスおよび
(または)非酸性ガスとの混合ガスを、MgO、
ZnOおよびBeOの1種または2種以上からなる弱
塩基性金属酸化物を主体とする吸着剤に接触さ
せ、二酸化窒素を選択的に吸着することを特徴と
する。 本発明の別の態様は、強酸性ガスである二酸化
窒素と、弱酸性ガスである炭酸ガスおよび非酸性
ガスとの混合ガスを、MgO、ZnOおよびBeOの
1種または2種以上からなる弱塩基性金属酸化物
を主体とする吸着剤を充填した第1充填層に導入
してこの混合ガス中の二酸化窒素を選択的に吸着
分離し、ついで第1充填層から流出した混合ガス
を強塩基性金属酸化物を主体とする吸着剤を充填
した第2充填層に導入し、混合ガス中の炭酸ガス
を選択的に吸着分離し、非酸性ガスを第2充填層
から流出させることを特徴とする。
[Means for solving the problem] Generally, base adsorbents adsorb acidic gases, but
The inventor discovered that among basic adsorbents, adsorbents with weak basic strength, particularly magnesium oxide, zinc oxide, and beryllium oxide, adsorb strongly acidic nitrogen dioxide but not weakly acidic carbon dioxide. Ta. The basic aspect of the present invention, which was completed based on the above findings, is to use a mixed gas of nitrogen dioxide, which is a strongly acidic gas, and carbon dioxide, which is a weakly acidic gas, and/or a non-acidic gas. , MgO,
It is characterized by selectively adsorbing nitrogen dioxide by contacting with an adsorbent mainly composed of a weakly basic metal oxide consisting of one or more of ZnO and BeO. Another aspect of the present invention is to use a mixed gas of nitrogen dioxide, which is a strongly acidic gas, and carbon dioxide, which is a weakly acidic gas, and a non-acidic gas, with a weak base consisting of one or more of MgO, ZnO, and BeO. Nitrogen dioxide in this mixed gas is selectively adsorbed and separated by introducing it into a first packed bed filled with an adsorbent mainly composed of oxidized metal oxides, and then the mixed gas flowing out from the first packed bed is treated with a strong base. It is characterized by introducing the gas into a second packed bed filled with an adsorbent mainly composed of metal oxides, selectively adsorbing and separating carbon dioxide gas in the mixed gas, and causing non-acidic gas to flow out from the second packed bed. .

【作用】[Effect]

この発明では、弱塩基性金属酸化物を主体とす
る吸着剤を用いることにより、常温で混合ガスの
中から二酸化窒素を選択的に分離または除去する
ことができる。それに加えて、二参加窒素の吸着
捕集後に吸着層を加熱することにより、吸着され
ていた二酸化窒素を放出させて回収し、同時に吸
着剤を再生することができる。したがつて、省エ
ネルギー的、省資源的なガスの分離が実現する。
この利点は、従来、空気中の二酸化窒素除去法の
ひとつとして行なわれている接触還元法では、接
触還元用触媒の充填層を常時350℃前後の高温に
保つ必要があること比較すれば、容易に理解され
るであろう。 また、接触還元法では二酸化窒素を100%除去
することが困難であるのに対し、本発明では、吸
着剤充填層が酸性ガスの飽和吸着による吸着破過
が起るまでの期間は、完全に二酸化窒素を分離す
ることができる。 さらに、常温吸着を利用して可動性、携帯性の
よい装置として設計することができるので、小規
模の非定常的な用途への応用が可能となる。
In this invention, by using an adsorbent mainly composed of a weakly basic metal oxide, nitrogen dioxide can be selectively separated or removed from a mixed gas at room temperature. In addition, by heating the adsorption layer after the adsorption and collection of the divalent nitrogen, the adsorbed nitrogen dioxide can be released and recovered, and the adsorbent can be regenerated at the same time. Therefore, energy-saving and resource-saving gas separation is realized.
This advantage is simple compared to the conventional catalytic reduction method used as a method for removing nitrogen dioxide from the air, which requires the packed bed of catalyst for catalytic reduction to be kept at a high temperature of around 350°C at all times. will be understood. In addition, while it is difficult to remove 100% of nitrogen dioxide with the catalytic reduction method, in the present invention, the adsorbent packed bed completely removes nitrogen dioxide during the period until adsorption breakthrough occurs due to saturated adsorption of acidic gas. Nitrogen dioxide can be separated. Furthermore, since it can be designed as a highly mobile and portable device by utilizing room-temperature adsorption, it can be applied to small-scale, unsteady applications.

【実施態様】[Embodiment]

本発明で吸着剤に用いる弱塩基性金属酸化物と
しては、酸化マグネシウム、酸化亜鉛および酸化
ベリリウムの1種または2種以上からえらぶ。 下記の表は、種々の金属酸化物、金属イオン交
換体および多孔性吸着剤の二酸化窒素(NO2)
に対する吸着特性を測定した結果を示す。また、
第1図は、その測定装置の1例を示し、窒素ボン
ベ1から窒素ガスN2を、流量調節装置2A,2
Bを通して10ml/分の一定流速で抜き出し、その
一方を二酸化窒素発生器3に通した後、恒温槽4
(25℃)で両者を混合して、NO2濃度0.49%
(v/v)とし、これを槽内の吸着剤充填層5に
導入し、充填層5から流出した気流はオートサン
プラー6を備えたガスクロマトグラフ7に導入
し、6分間隔でNO2漏洩濃度を測定するように
したもので、吸着剤はそれぞれ100mgを内径4mm
のガラス管に充填して用いた。
The weakly basic metal oxide used in the adsorbent in the present invention is selected from one or more of magnesium oxide, zinc oxide, and beryllium oxide. The table below shows the nitrogen dioxide (NO 2 ) concentration of various metal oxides, metal ion exchangers and porous adsorbents.
The results of measuring the adsorption characteristics of Also,
FIG. 1 shows an example of the measuring device, in which nitrogen gas N 2 is supplied from a nitrogen cylinder 1 to flow rate adjusting devices 2A and 2.
B through B at a constant flow rate of 10 ml/min, and after passing one side through nitrogen dioxide generator 3,
Mix both at (25℃) to obtain a NO 2 concentration of 0.49%.
(v/v) and introduced into the adsorbent packed bed 5 in the tank, and the airflow flowing out from the packed bed 5 was introduced into a gas chromatograph 7 equipped with an autosampler 6, and the NO 2 leakage concentration was measured at 6 minute intervals. It was designed to measure 100 mg of adsorbent each with an inner diameter of 4 mm.
It was used by filling it into a glass tube.

【表】【table】

【表】 表から明らかなように、種々の金属酸化物の中
で、弱塩基性酸化物である酸化マグネシウム
(MgO)と酸化亜鉛(ZnO)に、特異的に大きい
NO2の吸着量がみられ、酸化ベリリウム(BeO)
もこれに次いで大きな吸着量を示す。 これらの金属酸化物は、比表面積が小さいこ
と、NO2の吸着分子数がこれらの固体中で金属
原子数より大きいことから、NO2は表面に吸着
するだけでなく、内部へも吸収されるものと考え
られる。 これに対し、他の遷移金属酸化物MnO2、
V2O5、CuO、Fe2O3、TiO2などもNO2吸着を示
すが、その吸着量は少ない。また、活性炭、シリ
カゲル、ゼオライトなどの多孔性吸着剤のNO2
吸着量は、その比表面積の大きさから予想される
よりもはるかに少なく、弱塩基性金属酸化物の15
〜30%程度にすぎない。さらに、金属担持の陽イ
オン交換樹脂の場合も、上記の遷移金属酸化物と
同様に顕著な効果がみられない。 本発明で使用する塩基性金属酸化物の形態は、
市販の粉末状の試薬あるいは工業用製品をそのま
ま使用しても差支えないが、酸性ガスや水蒸気を
大量に吸着すると潮解現象に似た変化が起き、充
填使用したときに目詰りを起したり、再生が困難
になるおそれがある。そこで、塩基性金属酸化物
を単独で造粒せずに、その担体となるような強固
な担体、造粒用のバインダ、造粒した金属酸化物
に多孔性を賦与するための賦活剤などを添加し
て、球状、円柱状、ペレツトなどに造粒し、加熱
などの熱処理によつて熟成するのが好ましい。こ
のような担体としては、酸化チタン、シリカゲ
ル、アルミナ、シリコンカーバイド、軽石など一
般に使用されているものを挙げることができる。 次に、この発明による酸性ガスの吸着分離法を
図面を参照して具体的に説明する。 第2図はこの発明による、MgO、ZnOおよび
BeOの1種または2種以上からなる弱塩基性金
属酸化物を主体とする吸着剤(以下、「弱塩基性
吸着剤」という。)のみを用いた方法を示す。す
なわち、弱塩基性吸着剤としてペレツト状の酸化
亜鉛を充填した充填層の一端から二酸化炭素
(CO2)と二酸化窒素(NO2)を含む空気を流入
させると、強酸性ガスである二酸化窒素は充填層
により吸着捕集され、弱酸性ガスである二酸化炭
素は吸着されずに他端から空気とともに放出され
る。二酸化窒素を吸着した酸化亜鉛は、混合空気
の流入停止後、450℃程度に加熱して清浄な空気
を通すと、二酸化窒素を放出し、吸着剤として再
生することができる。 第3図は塩基強度の異なる二種類の吸着剤を用
いた方法を示す。すなわち、上記と同様に弱塩基
性吸着剤として酸化亜鉛を充填した第1充填層
に、強塩基性吸着剤としソーダライムを充填した
第2充填層が直列に接続されている。第1充填層
の入口側から二酸化炭素と二酸化窒素を含む空気
を流入させると、第1充填層では二酸化窒素を、
第2充填層では二酸化炭素をそれぞれ選択的に吸
着分離し、第2充填層からは酸性ガスを含まない
空気が流出する。 第4図は第3図の第1、第2充填層に脱水剤と
多孔性吸着剤を組合せた方法を示す。すなわち、
直列に接続した第1充填層の入口側には粒状硫酸
ナトリウムなどの脱水剤を充填した脱水層を、第
2充填層の出口側には活性炭のような非選択性の
多孔性吸着剤を充填した層を、それぞれ接続して
用いる。 この場合には、脱水層側から、二酸化窒素、二
酸化炭素および水蒸気のほか炭化水素やハロゲン
化炭化水素などの非酸性有機化合物の蒸気を含む
空気を導入すると、最初に脱水層で水分が除去さ
れ、第1および第2充填層で二酸化窒素、二酸化
炭素が順次吸着除去されたのち、多孔性吸着層に
おいて有機物蒸気が吸着除去され、最後の層から
は酸性ガスや有機物蒸気を含まない清浄な空気が
流出する。このようにして、酸性ガスや有機物蒸
気が、順次選択的に吸着分離される。 この場合にも、第1充填層において一定量の二
酸化窒素を吸着したのち、混合空気の流入を止め
て第1充填層を加熱し、清浄な空気を導入するこ
とにより、二酸化窒素を脱着し、吸着剤を再生す
ることができる。また、第2充填層および多孔性
吸着剤層については、上記と同様に脱着再生でき
る場合と、使用済の吸着剤を充填層から取り出
し、新しい吸着剤と交換する場合がある。
[Table] As is clear from the table, among various metal oxides, magnesium oxide (MgO) and zinc oxide (ZnO), which are weakly basic oxides, have a particularly large
Adsorption amount of NO 2 is observed, and beryllium oxide (BeO)
Also shows the second largest amount of adsorption. Because these metal oxides have a small specific surface area and the number of NO 2 adsorbed molecules is greater than the number of metal atoms in these solids, NO 2 is not only adsorbed on the surface but also absorbed into the interior. considered to be a thing. In contrast, other transition metal oxides MnO 2 ,
V 2 O 5 , CuO, Fe 2 O 3 , TiO 2 and the like also exhibit NO 2 adsorption, but the amount of adsorption is small. Also, porous adsorbents such as activated carbon, silica gel, and zeolite can reduce NO2
The amount of adsorption is much lower than expected from its large specific surface area, and is
It is only about ~30%. Furthermore, in the case of metal-supported cation exchange resins, no remarkable effect is observed, as in the case of the above-mentioned transition metal oxides. The form of the basic metal oxide used in the present invention is:
Commercially available powdered reagents or industrial products can be used as they are, but if they absorb a large amount of acidic gas or water vapor, a change similar to deliquescence will occur, which may cause clogging when filled and used. Playback may become difficult. Therefore, instead of granulating the basic metal oxide alone, we use a strong carrier, a binder for granulation, an activator to impart porosity to the granulated metal oxide, etc. It is preferable to add it, granulate it into spheres, cylinders, pellets, etc., and ripen it by heat treatment such as heating. Examples of such carriers include commonly used carriers such as titanium oxide, silica gel, alumina, silicon carbide, and pumice. Next, the acid gas adsorption separation method according to the present invention will be specifically explained with reference to the drawings. Figure 2 shows MgO, ZnO and
A method using only an adsorbent (hereinafter referred to as "weakly basic adsorbent") mainly composed of a weakly basic metal oxide consisting of one or more types of BeO is shown. In other words, when air containing carbon dioxide (CO 2 ) and nitrogen dioxide (NO 2 ) is introduced from one end of a packed bed filled with zinc oxide pellets as a weakly basic adsorbent, nitrogen dioxide, a strongly acidic gas, is released. The packed bed adsorbs and collects carbon dioxide, which is a weakly acidic gas, and is released from the other end along with air without being adsorbed. Zinc oxide that has adsorbed nitrogen dioxide can be heated to about 450°C after the inflow of mixed air is stopped and clean air is passed through it to release nitrogen dioxide and regenerate it as an adsorbent. Figure 3 shows a method using two types of adsorbents with different base strengths. That is, similarly to the above, a second packed bed filled with soda lime as a strong basic adsorbent is connected in series to a first packed bed filled with zinc oxide as a weak basic adsorbent. When air containing carbon dioxide and nitrogen dioxide is introduced from the inlet side of the first packed bed, nitrogen dioxide is
In the second packed bed, carbon dioxide is selectively adsorbed and separated, and air containing no acid gas flows out from the second packed bed. FIG. 4 shows a method in which a dehydrating agent and a porous adsorbent are combined in the first and second packed beds shown in FIG. That is,
The inlet side of the first packed bed connected in series is filled with a dehydrating layer filled with a dehydrating agent such as granular sodium sulfate, and the outlet side of the second packed bed is filled with a non-selective porous adsorbent such as activated carbon. The layers are connected and used. In this case, if air containing vapors of non-acidic organic compounds such as hydrocarbons and halogenated hydrocarbons in addition to nitrogen dioxide, carbon dioxide, and water vapor is introduced from the dehydration layer side, water is first removed in the dehydration layer. After nitrogen dioxide and carbon dioxide are sequentially adsorbed and removed in the first and second packed beds, organic vapors are adsorbed and removed in the porous adsorption layer, and from the last layer, clean air containing no acid gas or organic vapors is produced. flows out. In this way, acidic gases and organic vapors are sequentially and selectively adsorbed and separated. In this case as well, after adsorbing a certain amount of nitrogen dioxide in the first packed bed, the inflow of mixed air is stopped, the first packed bed is heated, and clean air is introduced to desorb nitrogen dioxide. The adsorbent can be regenerated. Further, regarding the second packed bed and the porous adsorbent layer, there are cases where desorption and regeneration can be performed in the same manner as described above, and cases where the used adsorbent is taken out from the packed bed and replaced with a new adsorbent.

【実施例】【Example】

次に、この発明を実施例により具体的に説明す
る。なお、以下の説明において、部は重量部を表
わす。 実施例 1 酸化亜鉛20部、水酸化アルミニウム10部、ブド
ウ糖1部を混合し、次に、全体がケーキ状になる
まで(1:10)稀硝酸(約10部)を加え、さらに
45分間混合した。これをペレツト押出機でペレツ
トとし、空気中で550℃まで昇温し、550℃〜600
℃の間で2時間焼成した。これをそのまま自然に
冷却し、酸化亜鉛を主体とする吸着剤を調製し
た。 このペレツト状の吸着剤を、内径20mmのガラス
管に長さ40mmに充填し、二酸化窒素NO2(0.49%)
を含む空気を流速を変えて導入し、その流出ガス
の一部を第1図に測定装置に接続し、二酸化窒素
の漏洩濃度を測定した結果、つぎのような結果を
得た。 混合空気の流速 NO2の漏洩濃度 (ml/分) (ppm) 250 検出されない 500 〃 1000 50 2000 350 上の結果から明らかなように、流速250〜2000
ml/分の範囲では、NO2の漏洩濃度は0〜
350ppmであり、吸着分離率は原濃度(4900ppm)
に対し、93%以上に達し、実用的価値のきわめて
高いことがわかる。 実施例 2 塩基性炭酸亜鉛40部、水酸化アルミニウム10部
および粉末状ゼオライト10部を混合し、全体がケ
ーキ状になるまで(1:10)稀硝酸を加えて、さ
らに混合した。これを押出し成形機で円筒状粒子
とし、ロータリーキルンの中で550℃までゆつく
り昇温した。次に550℃〜600℃の間で約2時間焼
成したのち、自然に冷却し、酸化亜鉛を主体とす
る吸着剤を調製した。 この円筒状粒子からなる吸着剤を、実施例1と
同様に、内径20mmのガラス管に40mmに充填し、二
酸化窒素の濃度を変えて一定流速(500ml/分)
で導入し、その流出ガス中の二酸化窒素の漏洩濃
度を測定し、つぎの結果を得た。 混合ガス中の二酸化窒素 NO2の漏洩濃度 の濃度(%) (ppm) 0.01 検出されない 0.1 〃 0.5 〃 このデータか明らかなように、0.01〜0.5の広
い濃度範囲にわたつて、NO2の初期漏洩濃度は
検出されないほど低く、その吸着分離特性は安定
している。 発明の効果 この発明によれば、以上説明したように、常温
で二酸化窒素を選択的に吸着分離することがで
き、吸着分離された二酸化窒素は加熱などにより
脱着回収が可能であり、、吸収剤も再生、再利用
できるので、省エネルギーおよび省資源の面でも
実用的価値が高い。 また、常温で吸着分離されることから、可動
性、携帯性のよい装置として設計することがで
き、分析装置などの小規模な用途にも役立つ。
Next, the present invention will be specifically explained using examples. In addition, in the following description, parts represent parts by weight. Example 1 Mix 20 parts of zinc oxide, 10 parts of aluminum hydroxide, and 1 part of glucose, then add dilute nitric acid (approximately 10 parts) until the whole becomes cake-like (1:10), and then
Mixed for 45 minutes. This is made into pellets using a pellet extruder, heated to 550℃ in air, and then heated to 550℃~600℃.
It was baked for 2 hours at ℃. This was naturally cooled as it was to prepare an adsorbent mainly composed of zinc oxide. This pellet-like adsorbent was filled in a glass tube with an inner diameter of 20 mm to a length of 40 mm, and nitrogen dioxide NO 2 (0.49%) was filled.
The leaked nitrogen dioxide concentration was measured by introducing air containing nitrogen dioxide at different flow rates and by connecting a portion of the effluent gas to the measuring device shown in Figure 1.The following results were obtained. Mixed air flow rate NO 2 leakage concentration (ml/min) (ppm) 250 Not detected 500 〃 1000 50 2000 350 As is clear from the above results, the flow rate is 250 to 2000
In the ml/min range, the leakage concentration of NO2 is 0~
350ppm, and the adsorption separation rate is the original concentration (4900ppm)
However, it reached over 93%, which shows that it has extremely high practical value. Example 2 40 parts of basic zinc carbonate, 10 parts of aluminum hydroxide and 10 parts of powdered zeolite were mixed, and dilute nitric acid was added and further mixed until the whole became cake-like (1:10). This was formed into cylindrical particles using an extruder, and the temperature was slowly raised to 550°C in a rotary kiln. Next, the mixture was calcined at 550°C to 600°C for about 2 hours, and then naturally cooled to prepare an adsorbent mainly composed of zinc oxide. Similar to Example 1, this adsorbent made of cylindrical particles was filled to a depth of 40 mm in a glass tube with an inner diameter of 20 mm, and the concentration of nitrogen dioxide was varied at a constant flow rate (500 ml/min).
The leaked concentration of nitrogen dioxide in the effluent gas was measured, and the following results were obtained. Concentration of leakage concentration of nitrogen dioxide NO 2 in mixed gas (%) (ppm) 0.01 Not detected 0.1 〃 0.5 〃 As is clear from this data, the initial leakage of NO 2 over a wide concentration range of 0.01 to 0.5 The concentration is so low as to be undetectable, and its adsorption and separation properties are stable. Effects of the Invention According to the present invention, as explained above, nitrogen dioxide can be selectively adsorbed and separated at room temperature, and the adsorbed and separated nitrogen dioxide can be desorbed and recovered by heating, etc. Since it can also be recycled and reused, it has high practical value in terms of energy and resource conservation. In addition, since adsorption separation occurs at room temperature, it can be designed as a device with good mobility and portability, and is useful for small-scale applications such as analytical devices.

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

第1図は種々の固体による二酸化窒素の吸着特
性を測定する装置の説明図である。第2図、第3
図および第4図は、それぞれ本発明の方法の実施
態様を示す説明図である。 1……窒素ボンベ、2A,2B……流量調節装
置、3……二酸化窒素発生器、4……恒温槽、5
……吸着剤充填層、6……オートサンプラー、7
……ガスクロマトグラフ。
FIG. 1 is an explanatory diagram of an apparatus for measuring the adsorption characteristics of nitrogen dioxide by various solids. Figures 2 and 3
FIG. 4 is an explanatory diagram showing an embodiment of the method of the present invention, respectively. 1... Nitrogen cylinder, 2A, 2B... Flow rate adjustment device, 3... Nitrogen dioxide generator, 4... Constant temperature bath, 5
... Adsorbent packed bed, 6 ... Auto sampler, 7
……Gas chromatograph.

Claims (1)

【特許請求の範囲】 1 強酸性ガスである二酸化窒素と、弱酸性ガス
である炭酸ガスおよび(または)非酸性ガスとの
混合ガスを、MgO、ZnOおよびBeOの1種また
は2種以上からなる弱塩基性金属酸化物を主体と
する吸着剤に接触させ、二酸化窒素を選択的に吸
着することを特徴とする酸性ガスの吸着分離法。 2 弱塩基性金属酸化物を、アルミナ、シリカゲ
ル、酸化チタン、シリコンカーバイドおよび軽石
の1種または2種以上の担体に担持してなる吸着
剤を用いる特許請求の範囲第1項に記載の酸性ガ
スの吸着分離法。 3 強酸性ガスである二酸化窒素と、弱酸性ガス
である炭酸ガスおよび非酸性ガスとの混合ガス
を、MgO、ZnOおよびBeOの1種または2種以
上からなる弱塩基性金属酸化物を主体とする吸着
剤を充填した第1充填層に導入してこの混合ガス
中の二酸化窒素を選択的に吸着分離し、ついで第
1充填層から流出した混合ガスを強塩基性金属酸
化物を主体とする吸着剤を充填した第2充填層に
導入し、混合ガス中の炭酸ガスを選択的に吸着分
離し、非酸性ガスを第2充填層から流出させるこ
とを特徴とする酸性ガスの選択的逐次吸着分離
法。 4 前記第1充填層への導入に先立つて、混合ガ
スを脱水剤を充填した脱水層を通し、ガス中の水
分を除去する工程を含む特許請求の範囲第3項に
記載の酸性ガスの選択的逐次吸着分離法。 5 前記第2充填層から流出した混合ガスを、活
性炭、ゼオライトなどの多孔性吸着剤を充填した
層に導入して有機物を吸着除去する工程を含む特
許請求の範囲第3項または第4項に記載の酸性ガ
スの選択的逐次吸着分離法。
[Claims] 1. A mixed gas of nitrogen dioxide, which is a strongly acidic gas, and carbon dioxide, which is a weakly acidic gas, and/or a non-acidic gas, is made of one or more of MgO, ZnO, and BeO. An adsorption separation method for acidic gases, which is characterized by selectively adsorbing nitrogen dioxide by bringing it into contact with an adsorbent mainly composed of weakly basic metal oxides. 2. Acidic gas according to claim 1 using an adsorbent in which a weakly basic metal oxide is supported on one or more carriers of alumina, silica gel, titanium oxide, silicon carbide, and pumice. adsorption separation method. 3 A mixed gas of nitrogen dioxide, which is a strongly acidic gas, and carbon dioxide gas, which is a weakly acidic gas, and a non-acidic gas is mixed with a weakly basic metal oxide mainly consisting of one or more of MgO, ZnO, and BeO. Nitrogen dioxide in this mixed gas is selectively adsorbed and separated by introducing it into a first packed bed filled with an adsorbent, and then the mixed gas flowing out from the first packed bed is made into a mixture containing mainly strong basic metal oxides. Selective sequential adsorption of acidic gas, which is characterized by introducing the adsorbent into a second packed bed, selectively adsorbing and separating carbon dioxide gas in the mixed gas, and causing non-acidic gas to flow out from the second packed bed. Separation method. 4. Selection of the acidic gas according to claim 3, which includes the step of passing the mixed gas through a dehydration layer filled with a dehydrating agent to remove moisture in the gas prior to introduction into the first packed bed. sequential adsorption separation method. 5. Claim 3 or 4 includes a step of introducing the mixed gas flowing out from the second packed bed into a bed filled with a porous adsorbent such as activated carbon or zeolite to adsorb and remove organic matter. The selective sequential adsorption separation method for acidic gases described.
JP59252232A 1984-11-28 1984-11-28 Adsorptive separation of acidic gas Granted JPS61129027A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59252232A JPS61129027A (en) 1984-11-28 1984-11-28 Adsorptive separation of acidic gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59252232A JPS61129027A (en) 1984-11-28 1984-11-28 Adsorptive separation of acidic gas

Publications (2)

Publication Number Publication Date
JPS61129027A JPS61129027A (en) 1986-06-17
JPH0373326B2 true JPH0373326B2 (en) 1991-11-21

Family

ID=17234352

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59252232A Granted JPS61129027A (en) 1984-11-28 1984-11-28 Adsorptive separation of acidic gas

Country Status (1)

Country Link
JP (1) JPS61129027A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2741743B2 (en) * 1994-11-17 1998-04-22 工業技術院長 High temperature separation of carbon dioxide

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2243731A1 (en) * 1973-09-14 1975-04-11 Norton Co Alumina catalyst support contg. magnesium oxide - used for metal or metal oxide catalysts for sulphur dioxide removal

Also Published As

Publication number Publication date
JPS61129027A (en) 1986-06-17

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