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JPS6358613B2 - - Google Patents
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JPS6358613B2 - - Google Patents

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Publication number
JPS6358613B2
JPS6358613B2 JP55067772A JP6777280A JPS6358613B2 JP S6358613 B2 JPS6358613 B2 JP S6358613B2 JP 55067772 A JP55067772 A JP 55067772A JP 6777280 A JP6777280 A JP 6777280A JP S6358613 B2 JPS6358613 B2 JP S6358613B2
Authority
JP
Japan
Prior art keywords
oxygen
adsorption
nitrogen
dissolved
type zeolite
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
Application number
JP55067772A
Other languages
Japanese (ja)
Other versions
JPS56163753A (en
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 filed Critical
Priority to JP6777280A priority Critical patent/JPS56163753A/en
Priority to EP81302162A priority patent/EP0040935B1/en
Priority to DE8181302162T priority patent/DE3171473D1/en
Publication of JPS56163753A publication Critical patent/JPS56163753A/en
Priority to US06/516,541 priority patent/US4453952A/en
Publication of JPS6358613B2 publication Critical patent/JPS6358613B2/ja
Granted legal-status Critical Current

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  • Separation Of Gases By Adsorption (AREA)
  • Oxygen, Ozone, And Oxides In General (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Silicates, Zeolites, And Molecular Sieves (AREA)

Description

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

本発明は、空気中の酸素を分離、除去、又は濃
縮するための酸素選択的吸着剤及びそれを使用し
ての酸素と窒素の分離方法に関する。 空気からの酸素の分離、除去、又は濃縮に於け
る最大の問題点は、通常原料を空気に求めるため
原料コストは存せず、酸素に付加される価格が (a) 分離、濃縮に設けられる設備費 (b) 装置を稼動させるに必要な諸動力費 (c) 分離媒体が必要な場合、その価格及び補充費
用 等に依存することである。 又、分離、濃縮のプロセスは原料を空気に求め
る限り酸素の分離、窒素の分離の二つの方法のい
ずれをとつてもかまわない。 これらの点から経済的に有利なものとしては、
従来実施されてきた酸素、窒素、分離プロセスの
代表的なものとして、空気を極低温に冷却し酸
素、窒素の沸点の違いにより分離する深冷分離装
置が挙げられる。この装置は、大容量の酸素製造
に適しており国内の酸素、窒素製造の大半が深冷
分離プロセスに依存しているが、大電力、大設備
を要するという欠点がある。 他には、近年ユニオンカーバイド社等により開
発され実用化されている分離方法に、アルミノシ
リケート系高分子吸着剤を使用したものがある。
このうち、モレキユラーシーブス5A,13X(ユニ
オンカーバイド社製、商品名)と称されるもの
は、窒素に対して極めて大きな吸着能(1.2g
N2/100gat NTP)を有し、これらにより空気
中から窒素の選択的除去を行ない酸素を分離、濃
縮するプロセスが実用化されている。実際には、
5A,13X型モレキユラーシーブスは、その吸着
能がラングミユア(Langmuir)型吸着等温線に
従い、圧力が1.5ataに達すると圧力の増加に比し
あまり吸着能が伸びないこと、又、空気中N2
O2モル比が4のため、極めて多量の窒素の除去
が必要となる。そのため、装置の大容量化にとも
なうスケールメリツトが小さく、小容量設備に限
定されているのが実状である。 又他には、酸素を選択的に吸収する遷移金属系
の有機錯体の利用も考えられる。 例えば、サルコミンと呼ばれる環状コバルト錯
体は、2モルのサルコミンで1モルの酸素を吸収
する。この吸収は、温度、圧力の変動に対して可
逆的であるので空気の昇温−降温サイクル、昇圧
−降圧サイクルにより原理的には酸素の分離、濃
縮が達成される。実際には吸収、放出にともない
劣化が甚だしく、又、高価なため、適用は極めて
特殊な酸素キヤリアーとしての使用に限定されよ
う。 これらの他、未だに実用化に至らないが原理的
にも充分に可能なものとして酸素選択透過フイル
ター、酸化ジルコニウムによる酸素ポンプ等が挙
げられる。 以上のように、酸素の分離、濃縮、除去に関し
ては実用上小容量酸素製造プロセスでは、モレキ
ユラーシーブスによる空気中の窒素除去による圧
力スイングプロセスが採用されている。又、大容
量型では空気の極低温冷却による深冷分離プロセ
スが採用されているが、いずれも動力費、設備費
の低減に関してはほとんど限界に到達したと考え
られる。 本発明は上記の酸素製造装置の欠点を改善し、
酸素の優先的な吸着剤を供することにより大幅な
酸素製造価格の低減、酸素製造プロセスの大幅な
設備の小型化を達成することを目的として提案す
るものである。 本発明者等は、前述のモレキユラーシーブスの
うちNa−A型ゼオライトは、室温においては吸
着塔に充填し高圧で空気を流過しても殆ど酸素を
選択的に吸着せず、むしろ前述の5A,13Xと同
様に窒素選択型吸着剤として挙動するのに対し、
Na−A型ゼオライトに少くとも2価以上の荷数
を有する鉄を湿状態で接触させた後、450℃近傍
の温度条件で熱処理してNa−A型ゼオライト結
晶にFeを溶解させると酸素選択性が上昇しかつ
一成分系での酸素吸着量が増大する事を見出し
た。 又、低温になるに従い本来Na−A型ゼオライ
トも酸素、窒素2成分系において酸素選択吸着性
が増大することを本発明者等は発見したが、Fe
を溶解させたNa−A型ゼオライトはNa−A型ゼ
オライトに比し、より高温側で酸素選択性が優れ
ていることを更に発見した。 このようなFeを溶解したNa−A型ゼオライト
の酸素選択性については従来の酸素、窒素に対す
る吸着の研究においては何ら明示されていない。 本発明者等は上述のFeを溶解したNa−A型ゼ
オライトを得るために下記のような処理を行なつ
た。 先ず本発明者等は、UCC社製Na−A型ゼオラ
イト粉末を充分に水洗し更にNaCl水溶液で100℃
1時間煮沸後、再び水洗したものを原料として使
用した。これはNa−A型ゼオライト粉末には、
0.1wt%程度のK、0.05wt%程度のCa、0.05wt%
程度のMg等の不純物が通常混入しているが、上
記処理により全不純物量が0.1wt%以下になるよ
うに精製することができるからである。この中か
ら50gを分取しこれを1の純水に入れてスラリ
ー状になるように撹拌しながら、Feイオンの酸
化の進行を防ぐため、N2ガスでバブリングして
溶存酸素を除去した。この後FeCl3水溶液を滴下
して更に撹拌を1時間続けた。FeCl3はスラリー
水溶液がPH8.5〜9程度のため、Fe(OH)3コロイ
ドとして存在するものと思われるが、大部分は
Na−A型ゼオライト粉末へ付着する。 この後脱水して第1図に示すような吸着塔に充
填し、空気からの酸素吸着特性を確認した。本実
験においては、FeCl3の滴下液量を調整する事に
より、Fe2O3換算重量%で0.5w%、1w%の2種
類を調整した。 この後Feの付着したNa−A型ゼオライトから
真空過器を使用して水を除去し、この後空気浴
で100℃で予備乾燥してから、真空加熱浴で
0.1Torrの真空排気条件下、450℃で1時間加熱
して、FeをNa−A型ゼオライトに浴解させて作
製した。FeのNa−A型ゼオライトへの溶解の品
質管理には、ESRによる結晶内におけるFeの位
置及び走査型電子顕微鏡による結晶断面のFeの
濃度分布により確認している。 なお、Na−A型ゼオライトへのFeの溶解に
は、上記FeCl3以外に、FeCl2、Fe(CH3CO22
Fe(NO32,Fe(NO33等を使用したが最終的な
吸着性は変らない。おそらく、スラリー滴下後
Fe(OH)2,Fe(OH)3を形成し最終的には脱水に
伴いNa−A型ゼオライトと
The present invention relates to an oxygen selective adsorbent for separating, removing, or concentrating oxygen in the air, and a method for separating oxygen and nitrogen using the same. The biggest problem in separating, removing, or concentrating oxygen from air is that since the raw material is usually air, there is no raw material cost, and the price added to oxygen is set for (a) separation and concentration. Equipment costs (b) Power costs necessary to operate the equipment (c) If a separation medium is required, it depends on its price and replenishment costs. Further, the separation and concentration process may be carried out by either of the two methods, oxygen separation or nitrogen separation, as long as air is used as the raw material. From these points of view, the economically advantageous ones are:
A typical example of a conventional oxygen/nitrogen separation process is a cryogenic separation device that cools air to an extremely low temperature and separates oxygen and nitrogen based on their different boiling points. This device is suitable for large-capacity oxygen production, and most of the domestic oxygen and nitrogen production relies on the cryogenic separation process, but it has the disadvantage of requiring large amounts of electricity and large equipment. Another separation method recently developed and put into practical use by Union Carbide and others uses an aluminosilicate polymer adsorbent.
Among these, molecular sieves 5A and 13X (manufactured by Union Carbide, trade name) have extremely high adsorption capacity for nitrogen (1.2g
N2 /100gat NTP), and a process for selectively removing nitrogen from the air and separating and concentrating oxygen has been put into practical use. in fact,
The adsorption capacity of 5A and 13X type molecular sieves follows the Langmuir type adsorption isotherm, and when the pressure reaches 1.5 ata, the adsorption capacity does not increase as much as the pressure increases. 2 /
Due to the O 2 molar ratio of 4, a very large amount of nitrogen needs to be removed. Therefore, the merits of scale associated with increasing the capacity of the device are small, and the actual situation is that the device is limited to small-capacity equipment. Another possibility is to use a transition metal-based organic complex that selectively absorbs oxygen. For example, a cyclic cobalt complex called sarcomine absorbs 1 mole of oxygen with 2 moles of sarcomine. Since this absorption is reversible with respect to changes in temperature and pressure, separation and concentration of oxygen can be achieved in principle by the heating-lowering cycle and pressure-raising-lowering cycle of the air. In reality, the deterioration due to absorption and release is severe, and since it is expensive, its application will be limited to use as a very special oxygen carrier. In addition to these, there are oxygen selective permeation filters, oxygen pumps using zirconium oxide, etc. that have not yet been put into practical use but are sufficiently possible in principle. As described above, in terms of oxygen separation, concentration, and removal, in practical small-capacity oxygen production processes, a pressure swing process is adopted in which nitrogen is removed from the air using molecular sieves. In addition, large-capacity types employ a cryogenic separation process using cryogenic cooling of air, but it is thought that all of these methods have almost reached their limits in terms of reducing power and equipment costs. The present invention improves the drawbacks of the above oxygen production equipment,
This proposal aims to significantly reduce the cost of oxygen production and significantly downsize the equipment for the oxygen production process by providing a preferential adsorbent for oxygen. The present inventors have discovered that among the above-mentioned molecular sieves, Na-A type zeolite hardly selectively adsorbs oxygen even when it is packed in an adsorption tower and air is passed through it at high pressure at room temperature; Although it behaves as a nitrogen selective adsorbent like 5A and 13X,
After contacting Na-A type zeolite with iron having a charge number of at least two or more in a wet state, heat treatment is performed at a temperature of around 450°C to dissolve Fe in the Na-A type zeolite crystals, which selects oxygen. It was found that the properties of the two components increased and the amount of oxygen adsorbed in a one-component system increased. In addition, the present inventors discovered that as the temperature decreases, Na-A type zeolite also increases its selective adsorption of oxygen in a two-component system of oxygen and nitrogen.
It was further discovered that the Na-A zeolite dissolved in Na-A zeolite has superior oxygen selectivity at higher temperatures than the Na-A zeolite. The oxygen selectivity of such Na-A type zeolite in which Fe is dissolved has not been clarified at all in conventional studies on adsorption of oxygen and nitrogen. The present inventors carried out the following treatment in order to obtain the above-described Fe-dissolved Na-A type zeolite. First, the present inventors thoroughly washed Na-A type zeolite powder manufactured by UCC with water and further heated it at 100°C with an aqueous NaCl solution.
After boiling for 1 hour, the product was washed again with water and used as a raw material. This means that Na-A type zeolite powder has
K about 0.1wt%, Ca about 0.05wt%, 0.05wt%
This is because although a certain amount of impurities such as Mg are usually mixed in, the above treatment can purify the total amount of impurities to 0.1 wt% or less. From this, 50 g was taken out and added to the pure water from step 1. While stirring to form a slurry, dissolved oxygen was removed by bubbling with N 2 gas to prevent the progress of oxidation of Fe ions. After that, an aqueous FeCl 3 solution was added dropwise, and stirring was continued for an additional hour. FeCl 3 is thought to exist as Fe(OH) 3 colloid because the slurry aqueous solution has a pH of about 8.5 to 9, but most of it is
Adheres to Na-A type zeolite powder. Thereafter, it was dehydrated and packed into an adsorption tower as shown in FIG. 1, and its oxygen adsorption characteristics from air were confirmed. In this experiment, two types of Fe 2 O 3 equivalent weight %, 0.5 w % and 1 w %, were adjusted by adjusting the amount of FeCl 3 dropped. After this, water is removed from the Fe-adhered Na-A zeolite using a vacuum filter, and then pre-dried at 100℃ in an air bath, and then in a vacuum heating bath.
It was produced by heating at 450° C. for 1 hour under vacuum evacuation conditions of 0.1 Torr to cause Fe to dissolve in Na-A type zeolite. Quality control of dissolution of Fe into Na-A type zeolite is confirmed by checking the position of Fe in the crystal by ESR and the concentration distribution of Fe in the cross section of the crystal by scanning electron microscopy. In addition, in addition to the above-mentioned FeCl 3 , FeCl 2 , Fe(CH 3 CO 2 ) 2 , Fe(CH 3 CO 2 ) 2 ,
Although Fe(NO 3 ) 2 , Fe(NO 3 ) 3, etc. were used, the final adsorption properties did not change. Probably after slurry dripping
Fe(OH) 2 and Fe(OH) 3 are formed and eventually Na-A zeolite is formed as a result of dehydration.

【式】【formula】

【式】【formula】

【式】【formula】

【式】等の結合を形成するためと考え られる。 しかし詳細については現在のところ不明であ
る。 以下図を参照してFeを溶解したNa−A型ゼオ
ライトの空気からの吸着分離性について説明す
る。 第1図はNa−A型ゼオライトの空気分離特性
を計測するために本発明者等が試作した装置の概
略説明図である。 1は高圧の空気ボンベである。ボンベ1を出た
高圧空気は減圧器2を経てボンベ3に至る。減圧
器2とバルブ3の間にブルドン管式圧力計4が設
置され圧力の測定が可能であり本試験では減圧器
2とブルドン管式圧力計4により入口圧力を5ata
に設定した。内径10mmφ、長さ300mmのステンレ
ス製の吸着塔6に挿入された水洗直後の吸着剤7
は何らの吸着能も有しない。このため本試験では
−70℃〜600℃迄の温度調整可能な温度調節浴8
に吸着塔6を設置し、吸着剤前処理のためバルブ
3,5を閉じ、バルブ9を開にし真空ポンプ10
で吸着塔内を0.1Torrに減圧し、温度調節浴8を
450℃に設定して脱水を兼ねて熱処理を1時間行
なつた。その後再び室温に冷却してからバルブ3
及び5を開にして高圧空気を流過させフロート式
流量計11で流量を測定した後酸素濃度計12に
全量流入させて出口酸素濃度を計測し更にデータ
は自記式記録計13で記録した。 第1図に示すような実験装置で吸着塔6に
Feを全く溶解していないNa−A型ゼオライト粉
末、0.5w%Feを溶解したNa−A型ゼオライト
粉末、1w%Feを溶解したNa−A型ゼオライト
粉末を15g充填し入口ガス流量を100Nml/分、
入口空気圧力を5ataに設定して出口酸素濃度の経
時変化を測定した。室温(25℃)における出口酸
素濃度の経時変化の例を第2図に示す。 第2図において横軸14は、経過時間であり、
1目盛は1分である。 縦軸15はO2濃度であり単位は容量%である。
入口側酸素濃度を示すため、空気中酸素濃度20.8
%のところに基準線16を記した。 又第2図において、出口酸素濃度の経時変化曲
線を、Feを全く溶解してないNa−A型ゼオラ
イト粉末は実線で、0.5w%Feを溶解したNa−
A型合成ゼオライト粉末は破線で、1w%Feを
溶解したものは一点鎖線で示している。 第2図において先ずFeを全く溶解してないNa
−A型ゼオライトの出口酸素濃度の経時変化デー
タから説明する。本試料では、出口酸素濃度は、
初期に20.8%から18%迄低下しその後46%迄急速
に上昇してから徐々に減少し空気流通後約5分で
破過した。 このデータからわかるように吸着の初期におい
ては、単位時間当りの酸素の吸着量が窒素の吸着
量を上廻り、このため、出口酸素濃度は減少す
る。しかし時間の経過とともに単位時間当りの酸
素の吸着量を窒素の吸着量が上廻り出口酸素濃度
は上昇する。更に吸着剤が酸素、窒素に対し飽和
するため徐々に低下し入口側ガス濃度に等しくな
る。 一方、Na−A型ゼオライトの酸素、窒素1成
分系の吸着量に関しては、“吸着の基礎と設計、
北川、鈴木P.226”に記載されているように20℃、
1ataの条件下で1g当り6.2mlの窒素と2.2mlの酸
素を吸着する。 これらの事実を総合すると、吸着量において窒
素の方が3倍程度大きいので本来出口酸素濃度は
高くなる筈であるが、酸素の吸着剤への拡散速度
が窒素の拡散速度に比べ大きいため、上記のよう
な現象がおこるものと推定される。 しかしながら今迄述べたNa−A型ゼオライト
の空気からの酸素、窒素の分離性で判るように、
あまりにも酸素の選択的吸着性が弱く、実用的に
使用する事は、経済的に困難である。 本発明者等は、これらの点についてNa−A型
ゼオライトに前記の調整でFeを溶解させると、
従来の文献にも記載されていない新たな性質の生
ずる事を見出した。既ち、Feを全く溶解しない
Na−A型ゼオライトでは上記の如く弱い酸素選
択性しか示さなかつたのに、FeをNa−A型ゼオ
ライトに溶解させると溶解量の増加にともない出
口酸素濃度の最低値は減少し、又最高値も減少す
る。これは窒素の吸着速度が酸素の吸着速度に比
べ減少し、吸着塔のような動的吸着条件では、極
めて高い酸素の選択的吸着性が得られる事とな
る。 以下本発明の有効性をひきつづき第2図により
説明する。 0.5w%のFe溶解Na−A型ゼオライトでは出口
酸素濃度の最低値は14%、最高値は30%、1w%
のFe溶解Na−A型ゼオライトでは出口酸素濃度
の最低値は6%、最高値は24%となる。 これらの性質から判るようにFeのNa−A型ゼ
オライトへの溶解により酸素の吸着速度に比べ窒
素の吸着速度が著しく減少している事を示してい
る。 又、酸素の1成分系での等温吸着量を測定する
と、Feを全く溶解しない場合、25℃1ata条件下
で2.2ml/gであるのに対し、0.5w%Fe溶解した
ものでは3ml/g、1w%Fe溶解したものでは3.8
ml/gと増加している事からFeの溶解量の増加
にともなう出口酸素濃度の最低値の減少は酸素吸
着速度だけではなく、酸素吸着量の増加も寄与し
ているものと考えられる。 更に上記〜の吸着剤を使用し、室温以下の
温度に冷却してから空気からの酸素吸着を行なつ
たところ室温における性質以外に新たな現象が生
じた。 第3図は0℃の出口酸素濃度の経時変化、第4
図は−30℃での出口酸素濃度の経時変化のデータ
である。 第3図に示すように、0℃の条件下において
は、〜のいずれの吸着剤も出口酸素濃度の最
低値は減少し、特に0.5w%Fe溶解のものでは
1.5vol%と出口では殆ど検出されていない。又出
口酸素濃度の最高値も〜のいずれのものでも
低下しており特に1w%Feを溶解したものでは全
く吸着されない。 更に第4図に示すように−30℃の条件下におい
ては、Feを全く溶解しないNa−A型ゼオライト
が最も出口酸素濃度の最低値が低く(1.5vol%)、
Feの溶解量の増加に判ない出口酸素濃度の最低
値は上昇する。しかし本実験においてはFeを溶
解したものでは出口酸素濃度の最高値はいずれも
入口酸素濃度を超える事はなく、酸素吸着速度が
低下しているだけで、酸素選択性はひき続き上昇
している。 以上の事例を要約すると、 (1) Na−A型ゼオライトにFeを溶解させるとFe
の溶解量の増加にともない、窒素吸着速度は酸
素吸着速度に比べ著しく低下し、吸着塔のよう
な動的吸着条件下では、著しく高い酸素選択性
を与える。 (2) Na−A型ゼオライト、及びそのFeを溶解し
たものはいずれも温度の低下にともない酸素選
択性が向上するが、その傾向はFeの溶解量の
大きなもの程顕著であり、動的吸着条件下にお
ける完全な酸素選択性はFeを溶解したものの
方が、Feを全く溶解しないものより、より高
温側で達成できる。 (3) Feを溶解したNa−A型ゼオライトではあま
りにも低温では、窒素吸着速度が全く無視し得
るとともに、酸素吸着速度の低下すら実用上さ
しつかえが出る程である。 以上説明したように本発明酸素吸着剤は、従来
の既文献にいかなる示唆もされていない酸素選択
型の全く新しい吸着剤であり、又Feを溶解しな
いNa−A型ゼオライトの1.5〜2倍の酸素を吸着
するという優れた利点を有する。 本発明酸素吸着剤は、その適用する範囲が極め
て広く例えばモレキユラーシーブスを利用した酸
素濃縮装置に適用する場合、温度スイング、圧力
スイング方式のいずれにも適用可能であり、従来
のN2吸着型モレキユラーシーブスの吸着性能を
はるかに凌駕し装置の小型化、酸素濃縮の低廉化
への道を開くものである。 又、本発明酸素吸着剤を他成分ガスから酸素除
去に利用するならば極めて安価な酸素吸着除去剤
を提供することとなる。 なお本発明における流量(100ml/分)、圧力
(5ata)条件下では、0℃迄の冷却でほぼ完全な
酸素選択性を示した。 なお、この条件下において流量、圧力、
吸着塔断面積、吸着塔長さ等によつてどのよう
に出口酸素濃度が変化するかは“吸着の基礎と設
計 北川、鈴木P.89〜92”により推定できる。 又この温度より高い側では、窒素の吸着速度が
無視し得ないため、2成分系について解析すれば
よい。 これらの結果によるとFeの溶解量が多い程又
低温になる程、酸素と窒素の物質移動係数が開く
事を意味し、これは実用的にはFeの溶解量が多
い程、低温になる程より低い入口流速が許容され
室温側ではより高い入口流速を設定しなければな
らない事となる。 いずれにしても、第2図〜第4図の出口酸素濃
度の経時変化データが得られれば吸着塔及びその
操作の設計は従来の技術範囲内で行ない得る。 なお、低温側温度条件の選定については上記吸
着剤の性質だけでは決らない。例えば廃熱が充分
に得られる条件下では吸収式冷凍機を使用しても
よくこの場合−25℃程度が最適であり、又他には
吸着塔を流過した後の高圧N2ガスとホルテツク
スチユーブを組み合わせると−10℃程度が最適で
あり、又、流過高圧N2ガスで膨脹タービンを駆
動すれば−30〜−50℃が好ましく、低温域の温度
選定はむしろ冷却の態様に依存する。 以下本発明の酸素の選択的吸着分離方法を圧力
スイング式酸素製造装置に適用した実施例につい
て説明する。 第5図は圧力スイング式酸素製造装置の概略説
明図である。第5図において、17〜24は自動
切換弁、25,26は本発明酸素吸着剤を充填し
た吸着塔、27は低温冷却用熱交、28は脱湿、
脱炭酸ガス用吸着塔、29はプレクーラ、30は
空気圧縮機、31は空気ストレーナ、32は絞り
弁であり、自動切換弁等を制御するための制御装
置等は図示を省略した。 今仮に、吸着塔25が吸着工程にあり、吸着塔
26が再生工程にあるとする。空気ストレーナ3
1を通つて除塵された空気は空気圧縮機30によ
り加圧されてから、プレクーラ29で粗脱水及び
室温迄冷却されて、更に吸着塔28で脱湿、脱炭
酸を行われてから、低温冷却熱交27で冷却され
て弁20を通つて吸着塔25に送入されて同塔内
の吸着剤に加圧空気中の酸素が選択的に吸着さ
れ、窒素富化空気が弁17を通つて同塔から送出
される。この時、吸着塔25に付設された弁1
7,20は開、弁18,19は閉となつている。 他方、吸着塔26は吸着塔25において吸着操
作を行なつている間に、まず吸着塔26内の吸着
剤の減圧再生を行なう。即ち、この時吸着塔26
に付設された弁21〜24のうち弁21,22,
24は閉、弁23は開とし吸着塔26内を大気圧
(または負圧)になるまで減圧して、吸着工程に
おいて吸着していた吸着成分の一部を脱着し、酸
素富化空気が弁23を通つて同塔から送出され
る。 減圧工程が終了すると同時に弁22が開とな
り、大気を送風手段(図示省略)により絞り弁3
2および弁22を通して吸着塔26内に送入し、
酸素に富んだ同塔内の空隙ガスおよび残吸着成分
を弁23を通じて同塔外に送出する掃気工程を行
なう。 上記の工程が終了すると同時に、吸着塔26は
吸着工程に移り同時に吸着塔25は再生工程に移
る。 上記の如く、吸着工程と再生工程を連続的に繰
返すことにより酸素富化空気および(又は)窒素
富化空気を取出すものである。 本発明の実施例では、内径50mm、長さ600mmの
吸着塔に1wt%のFeを溶解したNa−A型ゼオラ
イトを錠剤成型機で直径約1mmの球状に成型した
ものを1Kg充填し、供給空気圧力を1ata〜5ata間
でスイングし、入口空気流量を16Nl/分、温度
0℃の低温条件で吸着分離した。 この時の第5図における、バルブ17,21後
方の製品窒素濃度、同窒素分離量、バルブ19,
23後方の製品酸素濃度、同酸素回収量を第2表
に記す。 なお、25℃おいては、バルブ17,21の後方
からは製品窒素は得られず45%の酸素が流過し
た。これは、第1図に示す小型の空気分離試験機
で見られた吸着初期の酸素濃度のわずかの低下が
それに続く窒素吸着に打ち消されたためと思われ
る。25℃付近では、より大きな入口流速が必要で
あろう。
This is thought to be due to the formation of a bond such as [Formula]. However, details are currently unknown. The adsorption and separation properties of Na-A type zeolite in which Fe is dissolved from air will be explained below with reference to the figures. FIG. 1 is a schematic explanatory diagram of an apparatus prototyped by the present inventors to measure the air separation characteristics of Na-A type zeolite. 1 is a high pressure air cylinder. High pressure air leaving the cylinder 1 passes through a pressure reducer 2 and reaches the cylinder 3. A Bourdon tube pressure gauge 4 is installed between the pressure reducer 2 and the valve 3, and it is possible to measure the pressure.In this test, the inlet pressure was measured at 5ata using the pressure reducer 2 and the Bourdon tube pressure gauge 4
It was set to Adsorbent 7 immediately after washing inserted into a stainless steel adsorption tower 6 with an inner diameter of 10 mmφ and a length of 300 mm
does not have any adsorption capacity. For this reason, in this test, a temperature-controlled bath 8 whose temperature can be adjusted from -70℃ to 600℃ was used.
The adsorption tower 6 is installed at
The pressure inside the adsorption tower was reduced to 0.1 Torr, and the temperature control bath 8 was
Heat treatment was performed at 450°C for 1 hour, also serving as dehydration. Then, after cooling to room temperature again, valve 3
and 5 were opened to allow high-pressure air to flow through and measure the flow rate with a float type flow meter 11, and then the entire amount was allowed to flow into an oxygen concentration meter 12 to measure the outlet oxygen concentration, and the data was further recorded with a self-recording recorder 13. In the adsorption tower 6 using the experimental equipment shown in Figure 1,
Filled with 15g of Na-A type zeolite powder with no dissolved Fe, Na-A type zeolite powder with 0.5w% Fe dissolved, Na-A type zeolite powder with 1w% Fe dissolved, and the inlet gas flow rate was set to 100Nml/ minutes,
The inlet air pressure was set at 5ata and the change in outlet oxygen concentration over time was measured. Figure 2 shows an example of the change in outlet oxygen concentration over time at room temperature (25°C). In FIG. 2, the horizontal axis 14 is elapsed time;
One scale is one minute. The vertical axis 15 is the O 2 concentration, and the unit is volume %.
To indicate the oxygen concentration on the inlet side, the air oxygen concentration is 20.8
A reference line 16 is drawn at %. In addition, in Figure 2, the time-course curve of the outlet oxygen concentration is shown as a solid line for Na-A type zeolite powder with no dissolved Fe, and a solid line for Na-A zeolite powder with 0.5 w% Fe dissolved.
The A-type synthetic zeolite powder is shown by a broken line, and the powder containing 1w% Fe is shown by a dashed-dotted line. In Figure 2, first of all, Na has no dissolved Fe at all.
- This will be explained based on data on changes over time in outlet oxygen concentration of type A zeolite. In this sample, the outlet oxygen concentration is
It initially decreased from 20.8% to 18%, then rapidly increased to 46%, and then gradually decreased, reaching a breakthrough in about 5 minutes after air circulation. As can be seen from this data, at the initial stage of adsorption, the amount of oxygen adsorbed per unit time exceeds the amount of nitrogen adsorbed, and therefore the outlet oxygen concentration decreases. However, as time passes, the amount of nitrogen adsorbed exceeds the amount of oxygen adsorbed per unit time, and the outlet oxygen concentration increases. Furthermore, since the adsorbent becomes saturated with oxygen and nitrogen, the concentration gradually decreases and becomes equal to the gas concentration on the inlet side. On the other hand, regarding the adsorption amount of oxygen and nitrogen single component systems of Na-A type zeolite, please refer to “Basics and Design of Adsorption”.
20℃, as described in “Kitagawa, Suzuki P.226”
It adsorbs 6.2ml of nitrogen and 2.2ml of oxygen per 1g under 1ata condition. Taking all these facts together, the amount of nitrogen adsorbed is about three times larger, so the outlet oxygen concentration should originally be higher, but since the diffusion rate of oxygen into the adsorbent is greater than that of nitrogen, It is assumed that the following phenomenon occurs. However, as can be seen from the ability of Na-A zeolite to separate oxygen and nitrogen from air,
The selective adsorption of oxygen is too weak and it is economically difficult to use it practically. Regarding these points, the present inventors found that when Fe is dissolved in Na-A type zeolite with the above adjustment,
We have discovered that new properties that have not been described in conventional literature arise. Does not dissolve Fe at all
Although Na-A type zeolite showed only weak oxygen selectivity as mentioned above, when Fe was dissolved in Na-A type zeolite, the minimum value of the outlet oxygen concentration decreased as the amount of dissolved Fe increased, and the maximum value will also decrease. This means that the nitrogen adsorption rate is reduced compared to the oxygen adsorption rate, and under dynamic adsorption conditions such as in an adsorption tower, an extremely high selective adsorption of oxygen can be obtained. The effectiveness of the present invention will be explained below with reference to FIG. For 0.5w% Fe-dissolved Na-A type zeolite, the lowest value of outlet oxygen concentration is 14%, the highest value is 30%, 1w%
In the Fe-dissolved Na-A type zeolite, the minimum value of the outlet oxygen concentration is 6% and the maximum value is 24%. As can be seen from these properties, the dissolution of Fe into the Na-A type zeolite shows that the nitrogen adsorption rate is significantly reduced compared to the oxygen adsorption rate. In addition, when measuring the isothermal adsorption amount of oxygen in a one-component system, it is 2.2 ml/g at 25°C 1ata condition when no Fe is dissolved, whereas it is 3 ml/g when 0.5 w% Fe is dissolved. , 3.8 for 1w% Fe dissolved
ml/g, it is thought that the decrease in the minimum value of the outlet oxygen concentration with the increase in the amount of dissolved Fe is caused not only by the oxygen adsorption rate but also by the increase in the amount of oxygen adsorption. Furthermore, when the above adsorbents were used to adsorb oxygen from air after cooling to a temperature below room temperature, a new phenomenon occurred in addition to the properties at room temperature. Figure 3 shows the time course of the outlet oxygen concentration at 0°C, and Figure 4 shows the
The figure shows data on changes in outlet oxygen concentration over time at -30°C. As shown in Figure 3, under the condition of 0℃, the minimum value of the outlet oxygen concentration decreases for all of the adsorbents ~, especially for the 0.5w% Fe-dissolved one.
At 1.5vol%, it is hardly detected at the exit. Moreover, the maximum value of the outlet oxygen concentration also decreased in all of the cases of ~, and in particular, in the case of 1w% Fe dissolved therein, no adsorption was observed at all. Furthermore, as shown in Figure 4, under -30°C conditions, Na-A zeolite, which does not dissolve Fe at all, has the lowest outlet oxygen concentration (1.5 vol%);
The minimum value of the outlet oxygen concentration increases, which is not due to the increase in the amount of dissolved Fe. However, in this experiment, with dissolved Fe, the maximum outlet oxygen concentration never exceeded the inlet oxygen concentration, indicating that the oxygen adsorption rate was only decreasing, and the oxygen selectivity continued to increase. . To summarize the above cases, (1) When Fe is dissolved in Na-A type zeolite, Fe
As the dissolved amount of nitric acid increases, the nitrogen adsorption rate decreases significantly compared to the oxygen adsorption rate, and under dynamic adsorption conditions such as in an adsorption column, it provides a significantly high oxygen selectivity. (2) The oxygen selectivity of both Na-A type zeolite and its Fe-dissolved version improves as the temperature decreases, but this tendency is more pronounced as the amount of dissolved Fe increases, and dynamic adsorption Complete oxygen selectivity under these conditions can be achieved at higher temperatures with dissolved Fe than with no Fe dissolved at all. (3) In the case of Na-A type zeolite in which Fe is dissolved, at too low a temperature, the nitrogen adsorption rate can be completely ignored, and even a decrease in the oxygen adsorption rate is such that it becomes a practical problem. As explained above, the oxygen adsorbent of the present invention is a completely new oxygen-selective adsorbent that has not been suggested in any conventional literature, and it has an oxygen adsorption capacity of 1.5 to 2 times that of Na-A type zeolite, which does not dissolve Fe. It has the excellent advantage of adsorbing oxygen. The oxygen adsorbent of the present invention has a very wide range of applications, for example, when applied to oxygen concentrators using molecular sieves, it can be applied to both temperature swing and pressure swing methods, and can be applied to conventional N 2 adsorption methods. The adsorption performance far exceeds that of type molecular sieves, paving the way for smaller equipment and lower cost oxygen concentration. Furthermore, if the oxygen adsorbent of the present invention is used to remove oxygen from other component gases, an extremely inexpensive oxygen adsorption/removal agent will be provided. Note that under the conditions of flow rate (100 ml/min) and pressure (5 ata) in the present invention, almost perfect oxygen selectivity was exhibited upon cooling to 0°C. In addition, under this condition, the flow rate, pressure,
How the outlet oxygen concentration changes depending on the cross-sectional area of the adsorption tower, the length of the adsorption tower, etc. can be estimated from "Basics and Design of Adsorption Kitagawa, Suzuki, pp. 89-92." Furthermore, on the side higher than this temperature, the rate of nitrogen adsorption cannot be ignored, so it is sufficient to analyze a two-component system. According to these results, the larger the amount of Fe dissolved and the lower the temperature, the wider the mass transfer coefficients of oxygen and nitrogen become.Practically speaking, this means that the larger the amount of Fe dissolved, the lower the temperature becomes. A lower inlet flow rate is allowed, and a higher inlet flow rate must be set on the room temperature side. In any case, the design of the adsorption tower and its operation can be carried out within the conventional technical range if the data on the change in outlet oxygen concentration over time shown in FIGS. 2 to 4 are obtained. Note that the selection of the low-temperature conditions is not determined solely by the properties of the adsorbent. For example, an absorption chiller may be used under conditions where sufficient waste heat can be obtained, and in this case the optimal temperature is around -25℃. When combined with a tube tube, the optimum temperature is around -10℃, and when the expansion turbine is driven by flowing high-pressure N2 gas, the temperature between -30 and -50℃ is preferable, and the temperature selection in the low-temperature range rather depends on the mode of cooling. do. An example in which the method for selective adsorption and separation of oxygen of the present invention is applied to a pressure swing type oxygen production apparatus will be described below. FIG. 5 is a schematic explanatory diagram of a pressure swing type oxygen production apparatus. In FIG. 5, 17 to 24 are automatic switching valves, 25 and 26 are adsorption towers filled with the oxygen adsorbent of the present invention, 27 is a heat exchanger for low temperature cooling, 28 is a dehumidifier,
29 is a pre-cooler, 30 is an air compressor, 31 is an air strainer, 32 is a throttle valve, and a control device for controlling an automatic switching valve and the like is not shown. Assume now that the adsorption tower 25 is in the adsorption process and the adsorption tower 26 is in the regeneration process. air strainer 3
The air from which dust has been removed through 1 is pressurized by an air compressor 30, then roughly dehydrated and cooled to room temperature in a precooler 29, further dehumidified and decarboxylated in an adsorption tower 28, and then cooled at a low temperature. The air is cooled by a heat exchanger 27 and sent to an adsorption tower 25 through a valve 20, where oxygen in the pressurized air is selectively adsorbed by an adsorbent in the tower, and the nitrogen-enriched air is passed through a valve 17. Sent from the same tower. At this time, the valve 1 attached to the adsorption tower 25
7 and 20 are open, and valves 18 and 19 are closed. On the other hand, while the adsorption tower 25 is performing an adsorption operation, the adsorption tower 26 first performs vacuum regeneration of the adsorbent within the adsorption tower 26 . That is, at this time, the adsorption tower 26
Of the valves 21 to 24 attached to the valves 21, 22,
24 is closed and the valve 23 is opened to reduce the pressure inside the adsorption tower 26 to atmospheric pressure (or negative pressure), desorb some of the adsorbed components adsorbed in the adsorption process, and oxygen-enriched air flows through the valve. 23 and is sent out from the same tower. At the same time as the pressure reduction process is completed, the valve 22 is opened, and the atmosphere is sent to the throttle valve 3 by a blowing means (not shown).
2 and into the adsorption tower 26 through the valve 22,
A scavenging process is performed in which the oxygen-rich void gas and residual adsorbed components in the column are sent out of the column through the valve 23. At the same time as the above steps are completed, the adsorption tower 26 moves to the adsorption step, and at the same time, the adsorption tower 25 moves to the regeneration step. As mentioned above, oxygen-enriched air and/or nitrogen-enriched air are extracted by continuously repeating the adsorption step and the regeneration step. In the example of the present invention, an adsorption tower with an inner diameter of 50 mm and a length of 600 mm was filled with 1 kg of Na-A type zeolite in which 1 wt% Fe was dissolved and molded into a sphere with a diameter of about 1 mm using a tablet molding machine, and the supplied air was The pressure was swung between 1 ata and 5 ata, the inlet air flow rate was 16 Nl/min, and the adsorption separation was performed at a low temperature of 0°C. At this time, in FIG. 5, the product nitrogen concentration behind valves 17 and 21, the amount of nitrogen separated, the valve 19,
Table 2 shows the product oxygen concentration behind No. 23 and the amount of recovered oxygen. Note that at 25° C., no product nitrogen was obtained from behind the valves 17 and 21, and 45% of oxygen passed through. This seems to be because the slight decrease in oxygen concentration at the initial stage of adsorption, which was observed in the small air separation tester shown in Figure 1, was canceled out by the subsequent nitrogen adsorption. Around 25°C, higher inlet flow rates may be required.

【表】【table】

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

第1図は本発明に関しその効果を確認するため
に使用した実験装置のフロー、第2図,第3図及
び第4図は、実質的に純粋なNa−A型ゼオライ
ト並びにFe溶解量0.5wt%、1wt%のNa−A型ゼ
オライトの常温、0℃,−30℃の温度下の動的吸
着量を示すグラフ、第5図は本発明の実施態様の
フローを示す。
Figure 1 shows the flow of the experimental equipment used to confirm the effects of the present invention, and Figures 2, 3, and 4 show substantially pure Na-A zeolite and Fe dissolution amount of 0.5wt. %, a graph showing the dynamic adsorption amount of 1wt% Na-A type zeolite at room temperature, 0°C, and -30°C, and Fig. 5 shows the flow of the embodiment of the present invention.

Claims (1)

【特許請求の範囲】 1 実質的に純粋なNa−A型ゼオライトに少く
とも2価以上の荷数を有する鉄を溶解してなる酸
素、窒素2成分混合ガスからの酸素吸着剤。 2 室温以下の温度域で相対的に高い圧力の酸
素、窒素2成分混合ガスを実質的に純粋なNa−
A型ゼオライトに少くとも2価以上の荷数を有す
る鉄を溶解してなる酸素吸着剤充填層に流過させ
て酸素を該吸着剤に選択的に吸着させて窒素ガス
を採取し、次いで該吸着剤充填層を相対的に低い
圧力にして吸着酸素を採取することを特徴とする
酸素、窒素2成分混合ガスを酸素と窒素に分離す
る方法。
[Scope of Claims] 1. An oxygen adsorbent from a binary mixed gas of oxygen and nitrogen, which is obtained by dissolving iron having a charge number of at least two valences in substantially pure Na-A type zeolite. 2. Converting a binary gas mixture of oxygen and nitrogen at a relatively high pressure in a temperature range below room temperature to substantially pure Na-
Nitrogen gas is collected by passing through an oxygen adsorbent packed bed made by dissolving iron having a valence of at least two or more in A-type zeolite, and selectively adsorbing oxygen to the adsorbent. A method for separating a two-component mixed gas of oxygen and nitrogen into oxygen and nitrogen, which is characterized by collecting adsorbed oxygen by applying a relatively low pressure to an adsorbent packed bed.
JP6777280A 1980-05-23 1980-05-23 Oxygen adsorbent from oxygen and nitrogen two component gas and method for separation of oxygen and nitrogen by said adsorbent Granted JPS56163753A (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP6777280A JPS56163753A (en) 1980-05-23 1980-05-23 Oxygen adsorbent from oxygen and nitrogen two component gas and method for separation of oxygen and nitrogen by said adsorbent
EP81302162A EP0040935B1 (en) 1980-05-23 1981-05-15 Oxygen adsorbent and process for the separation of oxygen and nitrogen using same
DE8181302162T DE3171473D1 (en) 1980-05-23 1981-05-15 Oxygen adsorbent and process for the separation of oxygen and nitrogen using same
US06/516,541 US4453952A (en) 1980-05-23 1983-07-22 Oxygen absorbent and process for the separation of oxygen and nitrogen using the same

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6777280A JPS56163753A (en) 1980-05-23 1980-05-23 Oxygen adsorbent from oxygen and nitrogen two component gas and method for separation of oxygen and nitrogen by said adsorbent

Publications (2)

Publication Number Publication Date
JPS56163753A JPS56163753A (en) 1981-12-16
JPS6358613B2 true JPS6358613B2 (en) 1988-11-16

Family

ID=13354562

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6777280A Granted JPS56163753A (en) 1980-05-23 1980-05-23 Oxygen adsorbent from oxygen and nitrogen two component gas and method for separation of oxygen and nitrogen by said adsorbent

Country Status (1)

Country Link
JP (1) JPS56163753A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2019147697A (en) * 2018-02-26 2019-09-05 株式会社Ihi Oxygen gas production device

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JPS56163753A (en) 1981-12-16

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