JPH02207838A - Oxygen and nitrogen separation adsorbent, adsorption method and application equipment - Google Patents

Oxygen and nitrogen separation adsorbent, adsorption method and application equipment

Info

Publication number
JPH02207838A
JPH02207838A JP1025800A JP2580089A JPH02207838A JP H02207838 A JPH02207838 A JP H02207838A JP 1025800 A JP1025800 A JP 1025800A JP 2580089 A JP2580089 A JP 2580089A JP H02207838 A JPH02207838 A JP H02207838A
Authority
JP
Japan
Prior art keywords
adsorbent
oxygen
nitrogen
adsorption
type
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.)
Pending
Application number
JP1025800A
Other languages
Japanese (ja)
Inventor
Masaomi Tomomura
友村 政臣
Hisao Yamashita
寿生 山下
Akira Kato
明 加藤
Hiroshi Kawagoe
川越 博
Ryokichi Yamada
山田 良吉
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.)
Hitachi Ltd
Original Assignee
Hitachi Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hitachi Ltd filed Critical Hitachi Ltd
Priority to JP1025800A priority Critical patent/JPH02207838A/en
Publication of JPH02207838A publication Critical patent/JPH02207838A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B13/00Oxygen; Ozone; Oxides or hydroxides in general
    • C01B13/02Preparation of oxygen
    • C01B13/0229Purification or separation processes
    • C01B13/0248Physical processing only
    • C01B13/0259Physical processing only by adsorption on solids
    • C01B13/0262Physical processing only by adsorption on solids characterised by the adsorbent
    • C01B13/027Zeolites
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B2210/00Purification or separation of specific gases
    • C01B2210/0043Impurity removed
    • C01B2210/0046Nitrogen

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Analytical Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Oxygen, Ozone, And Oxides In General (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Separation Of Gases By Adsorption (AREA)

Abstract

PURPOSE:To efficiently produce an adsorbent for separating oxygen and nitrogen by subjecting zeolite based on silica and alumina to ion exchange with cations contg. Ca and Sr. CONSTITUTION:Zeolite based on silica and alumina and having a crystal structure of A type, X type, Y type, L type, etc., is subjected to ion exchange with cations contg. Ca and Sr to obtain an adsorbent for separating oxygen and nitrogen. An adsorption tower is packed with this adsorbent and a gaseous mixture contg. nitrogen and oxygen is passed through the tower to produce oxygen-rich gas. When the adsorbent is satd. with nitrogen, the feed of the gaseous mixture is stopped and nitrogen-rich gas is removed from the adsorbent. The pref. content of Sr is 0-65wt.% of the content of Ca at the time of producing the adsorbent.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、O2及びN2を含有する気体よりO2とN2
を分離する方法に係り、特に、吸着剤を用いて、気体中
の02とN2を分離濃縮する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention provides a method for reducing O2 and N2 from a gas containing O2 and N2.
The present invention relates to a method of separating 02 and N2 in a gas, and particularly to a method of separating and concentrating 02 and N2 in a gas using an adsorbent.

[従来の技術] 従来、OxとN2を含有する混合気体より02とN2を
分離する方法としては、例えば、その混合気体として空
気を例にとって述べれば、深冷分離法(空気の液化蒸留
法)、および、吸着法が実用化されている。
[Prior Art] Conventionally, as a method for separating 02 and N2 from a mixed gas containing Ox and N2, for example, taking air as the mixed gas, there is a cryogenic separation method (air liquefaction distillation method). , and adsorption methods have been put into practical use.

このうち、吸着剤を用いる吸着法では、分子ふるい作用
をするゼオライト系吸着剤や炭素質系の吸着剤が使用さ
れている。このゼオライト系吸着剤を用いてO2とN2
を分離する場合には、活性化された吸着剤を充填した吸
着塔を所定吸着圧力に到達するまで、目的製品ガスによ
って加圧しておき、これに吸着対象ガスを所定流速で通
じることにより窒素成分を選択的に吸着床に吸着させて
Among these, in the adsorption method using an adsorbent, a zeolite-based adsorbent or a carbonaceous-based adsorbent that acts as a molecular sieve is used. Using this zeolite adsorbent, O2 and N2
In order to separate nitrogen components, an adsorption tower filled with activated adsorbent is pressurized with the target product gas until it reaches a predetermined adsorption pressure, and the gas to be adsorbed is passed through this at a predetermined flow rate to separate nitrogen components. selectively adsorbed on an adsorption bed.

塔より放出される酸素富化ガス中で所定の酸素純度をも
つ部分を製品ガスとして、取り出すのが通例である。と
ころで、この吸着法によって得られる目的製品ガスの純
度や収率を向上させて装置の経済性をさらに高めるには
、吸着剤のNZ吸着容量の増加が必要である。
It is customary to take out a portion of the oxygen-enriched gas discharged from the tower that has a predetermined oxygen purity as a product gas. By the way, in order to improve the purity and yield of the target product gas obtained by this adsorption method and further increase the economic efficiency of the apparatus, it is necessary to increase the NZ adsorption capacity of the adsorbent.

吸着剤に関する発明のうち、イオン交換によって吸着性
能を改善するものは、特に、ゼオライトに単一成分をイ
オン交換するものは、特開昭61−35850号、同6
0−179134号、同62−27037号、同60−
139337号、同60−68052号公報があげられ
る。
Among inventions related to adsorbents, those that improve adsorption performance by ion exchange, especially those that ion exchange a single component with zeolite, are disclosed in JP-A-61-35850 and JP-A-61-35850.
No. 0-179134, No. 62-27037, No. 60-
139337 and 60-68052.

しかし、複数成分をイオン交換させたものはない。However, there is no product in which multiple components are ion-exchanged.

これらの発明のうち、N2を吸着分離した02を効率良
く回収する剤に関するものは、特開昭60−17913
4号と同60−68052号公報とがあげられる。
Among these inventions, one related to an agent for efficiently recovering 02 from which N2 has been adsorbed and separated is disclosed in Japanese Patent Application Laid-Open No. 17913/1986.
No. 4 and No. 60-68052.

特開昭60−179134号公報ではゼオライト13X
にBaを交換し、特開昭60−68052号公報ではN
a型ゼオライトにアルカリ土類金属をイオン交換するも
のである。これら発明では、単一成分のみをイオン交換
している。
In JP-A-60-179134, zeolite 13X
In JP-A No. 60-68052, N is replaced with Ba.
This method involves ion-exchanging alkaline earth metals with a-type zeolite. In these inventions, only a single component is ion-exchanged.

本発明では、シ、リカ及びアルミナを主成分とするゼオ
ライトにカルシウムとストロンチウムをイオン交換する
ことによってN2吸着容量の増加を図った。
In the present invention, the N2 adsorption capacity was increased by ion-exchanging calcium and strontium into a zeolite containing Si, LiCa, and alumina as main components.

【発明が解決しようとする課題〕[Problem to be solved by the invention]

従来の酸素製造プロセスの設備コストは高価であり、特
に、吸着剤コストは全設備コストの20%以上を占めて
いた。
Equipment costs for conventional oxygen production processes are expensive, and in particular, adsorbent costs account for more than 20% of the total equipment costs.

本発明では吸着剤のN2吸着容址の増大を図ることによ
って、使用吸着剤を減少し、設備コストの大幅な低減を
図ることを目的とした。
The present invention aims to increase the N2 adsorption capacity of the adsorbent, reduce the amount of adsorbent used, and significantly reduce equipment costs.

〔課題を解決するための手段〕[Means to solve the problem]

吸着法によりゼオライトがもつ効果は、二つの全く異な
った原理によって根拠づけることが出来る。
The effectiveness of zeolites in adsorption methods can be based on two completely different principles.

第一には、横断面の投影において、互いに異なる分子は
比較的小さな分子だけを均一なゼオライトの孔を通過さ
せることにより分離できるので、これらの分子の実際上
の吸着の空洞に接近することができる(ふるい効果)。
Firstly, in the cross-sectional projection, different molecules can be separated by passing only relatively small molecules through the pores of a homogeneous zeolite, so that the actual adsorption cavities of these molecules can be accessed. Yes (sieve effect).

第二に、ゼオライトの結晶内部の表面がもつ極性の性質
によって、より極性のある分子が極性の弱い分子に優先
して吸着され、分子の形状がゼオライト孔を通して接近
できれば、より強く極性化される分子がより弱く極性化
される分子に優先して吸着される(極性効果)。
Second, due to the polar nature of the internal surface of zeolite crystals, more polar molecules are adsorbed preferentially to less polar molecules, and the more the shape of the molecule can be accessed through the zeolite pores, the more polarized it becomes. Molecules are adsorbed preferentially to molecules that are more weakly polarized (polarization effect).

ゼオライトによって実用化された吸着技術はこのいずれ
か、ある場合には両方の原理が同時に作用する。ゼオラ
イトの孔径は陽イオンによって影響を受ける。合成した
場合には、ゼオライトは一般にNa型で得られる。この
ものは約4人の孔径(直経)をもつ、イオン交換法によ
り、Naイオンの代りにより容積が大きなにイオンを導
入することによって孔径を狭めることができる。他方。
The adsorption technology that has been put to practical use with zeolites uses either of these principles, and in some cases both principles work simultaneously. Zeolite pore size is influenced by cations. When synthesized, zeolites are generally obtained in the Na form. This material has a pore size (direct diameter) of about 4 people, and the pore size can be narrowed by introducing ions into a larger volume instead of Na ions using the ion exchange method. On the other hand.

Naイオンを二価のCaイオンと代えるならば、孔径を
拡大できる。その理由は、二つのNaイオンの代りに、
実質上同様なイオン半径をした唯一つのCaイオンが結
晶格子に入るからである。孔径の変化は、工業上の応用
に関する限り、重要な他の特性も変更されるが、ふるい
効果のために、ゼオライトの選択比に、当然、影響する
。この二価イオンの導入は結晶格子の極性を増大させ、
より速やかな分子の吸着、及び、脱着が促進できる。
If Na ions are replaced with divalent Ca ions, the pore size can be expanded. The reason is that instead of two Na ions,
This is because only one Ca ion with substantially similar ionic radius enters the crystal lattice. A change in pore size naturally affects the selectivity of the zeolite due to the sieving effect, although other properties of importance as far as industrial applications are concerned are also changed. The introduction of this divalent ion increases the polarity of the crystal lattice,
More rapid adsorption and desorption of molecules can be promoted.

本発明によるゼオライトは、結晶構造の違いにより、A
型、X型、Y型、L型、オフレタイト(Offreti
ta) 、エリオナイト([Er1onite−) 、
モルデナイト(Mordenite) 、フェリライト
(Ferrierite)及びZSM−5から選ばれた
少なくとも一種を使用する0本発明者等は、ゼオライト
にカルシウムとストロンチウムを含むカチオンで複合イ
オン交換することによって、吸着剤のN2吸着容量が大
幅に増大することを見いだした。
The zeolite according to the present invention has A
Type, X type, Y type, L type, Offretite
ta), Erionite ([Er1onite-),
Using at least one selected from mordenite, ferrierite, and ZSM-5, the present inventors have developed an adsorbent N2 It was found that the adsorption capacity was significantly increased.

このような、複合イオン交換型ゼオライトのN2吸着量
については、従来のNz、Ozに対する吸着研究では、
何ら明示されてはいなかった。
Regarding the N2 adsorption amount of such composite ion exchange type zeolite, in the conventional adsorption research for Nz and Oz,
Nothing was made clear.

本発明では、複合イオンとしてカルシウムとストロンチ
ウムを用い、ストロンチウムのイオン交換率が0〜65
wt%、好ましくは、10〜40wt%でのN2吸着量
が大きいことを明らかにした。
In the present invention, calcium and strontium are used as composite ions, and the ion exchange rate of strontium is 0 to 65.
It has been revealed that the amount of N2 adsorption is large at wt%, preferably 10 to 40 wt%.

〔実施例〕〔Example〕

以下1本発明の実施例について説明する。 An embodiment of the present invention will be described below.

く吸着容量測定方法〉 第4図は、本発明で得られる改質剤の性能を評価するた
めの02及びN2吸着容量測定装置であり、以下のよう
に測定する。吸着剤1をベッセル2(内径30m、高さ
55−)に8.0g充填し、真空ポンプ1でV−1を介
して脱着再生される。。
Adsorption Capacity Measuring Method> FIG. 4 shows a 02 and N2 adsorption capacity measuring device for evaluating the performance of the modifier obtained by the present invention, and the measurement is performed as follows. A vessel 2 (inner diameter 30 m, height 55-) is filled with 8.0 g of adsorbent 1, and is desorbed and regenerated by vacuum pump 1 via V-1. .

吸着剤5の温度は温度調節器4で調節した。一方、ベッ
セル3はV−6又はV−7を介して02.又は、N2で
予め加圧しておく、真空再生終了後、V−3のみを開放
しベッセル2及び3を連結して、ベッセル2の圧力変化
を圧力センサ6により測定する。圧力が一定値に収束す
るまで放置し、収束した値を平衡圧力とした。ベッセル
3から2へのN2ガス移動量、すなわち、N2吸着容量
はベッセル3の圧力計8の圧力変化から求めた。また、
ベッセル2内の温度変化は熱電対7で測定した。
The temperature of the adsorbent 5 was controlled by a temperature controller 4. On the other hand, Vessel 3 is connected to 02.02 via V-6 or V-7. Alternatively, after the vacuum regeneration is completed by pressurizing with N2 in advance, only V-3 is opened, vessels 2 and 3 are connected, and the pressure change in the vessel 2 is measured by the pressure sensor 6. The pressure was left until it converged to a constant value, and the converged value was taken as the equilibrium pressure. The amount of N2 gas transferred from the vessel 3 to the vessel 2, that is, the N2 adsorption capacity, was determined from the pressure change of the pressure gauge 8 of the vessel 3. Also,
The temperature change inside the vessel 2 was measured with a thermocouple 7.

測定終了後、ベッセル2及び3はV−5を介してHeガ
スでパージする。真空再生、ベッセル2゜3の連絡、H
eパージの各サイクルを繰り返えすことによって測定を
行なった。
After the measurement is completed, vessels 2 and 3 are purged with He gas via V-5. Vacuum regeneration, connection of vessel 2゜3, H
Measurements were made by repeating each cycle of e-purge.

まず、ゼオライトの結晶構造としてA型を使用し、カチ
オンとしてマグネシウム、カルシウム。
First, type A is used as the crystal structure of zeolite, and magnesium and calcium are used as cations.

ストロンチウム、バリウム、リチウム、マンガン。Strontium, barium, lithium, manganese.

ニッケル及びクロムの硝酸塩を用いてイオン交換した。Ion exchange was performed using nickel and chromium nitrates.

く比較例1〉 直径1fi1.長さ5mlの円柱状Na−A型ゼオライ
l−150gを原料とし、硝酸マグネシウム87gをI
Qの水に加え攪拌しながら少なくとも25℃で24時間
含浸させた後、水洗し、恒温槽で250℃、工時間焼成
し供試試料とし吸着容量測定法によって吸着容量を測定
した。
Comparative Example 1> Diameter 1fi1. Using 150 g of cylindrical Na-A type zeolite with a length of 5 ml as a raw material, 87 g of magnesium nitrate was added to I
It was added to the water of Q and impregnated at 25° C. for at least 24 hours with stirring, then washed with water and baked in a constant temperature bath at 250° C. for a working time to prepare a test sample, and the adsorption capacity was measured by the adsorption capacity measurement method.

く比較例2〉 直径1m、長さ5■の円柱状Na−A型ゼオライト15
0gを原料とし、硝酸カルシウム97gをIQの水に加
え攪拌しながら少なくとも25℃で24時間含浸させた
後、水洗し、恒温槽で250℃、工時間焼成した。
Comparative Example 2> Cylindrical Na-A type zeolite 15 with a diameter of 1 m and a length of 5 cm
Using 0g of calcium nitrate as a raw material, 97g of calcium nitrate was added to IQ water and impregnated with stirring at at least 25°C for 24 hours, washed with water, and baked at 250°C in a constant temperature bath for a working time.

く比較例3〉 イオン交換用に硝酸ストロンチウムを用い、他の操作は
実施例1と同様である。
Comparative Example 3> Strontium nitrate was used for ion exchange, and the other operations were the same as in Example 1.

〈比較例4〉 イオン交換用に硝酸バリウムを用い、他の操作は実施例
1と同様である。
<Comparative Example 4> Barium nitrate was used for ion exchange, and other operations were the same as in Example 1.

〈比較例5〉 イオン交換用に硝酸リチウムを用い、他の操作は実施例
1と同様である。
<Comparative Example 5> Lithium nitrate was used for ion exchange, and other operations were the same as in Example 1.

〈比較例6〉 イオン交換用に硝酸マンガンを用い、他の操作は実施例
1と同様である。
<Comparative Example 6> Manganese nitrate was used for ion exchange, and other operations were the same as in Example 1.

く比較例7〉 イオン交換用に硝酸ニッケルを用い、他の操作は実施例
1と同様である。
Comparative Example 7> Nickel nitrate was used for ion exchange, and the other operations were the same as in Example 1.

く比較例8〉 イオン交換用に硝酸クロムを用い、他の操作は実施例1
と同様である。
Comparative Example 8> Chromium nitrate was used for ion exchange, and the other operations were as in Example 1.
It is similar to

〈比較例9〉 Na−A型ゼオライトについて、吸着容量測定方法によ
ってN2の吸着容量を測定した。
Comparative Example 9 The N2 adsorption capacity of Na-A zeolite was measured by an adsorption capacity measuring method.

比較例1〜9の結果を温度25℃、吸着圧力0.25及
びQ、95ataでのN2吸着容量として整理した結果
を第1表に示す。
Table 1 shows the results of Comparative Examples 1 to 9 organized as N2 adsorption capacity at a temperature of 25°C, an adsorption pressure of 0.25, and a Q of 95ata.

第1表 第1表から、比較例2の場合、N2吸着容量が4 、8
 N cc / g  と最大値を示し、原料ゼオライ
トである比較例9と比べて約1.92倍増加した。
Table 1 From Table 1, in the case of Comparative Example 2, the N2 adsorption capacity is 4 and 8.
It showed the maximum value of N cc / g, which was about 1.92 times higher than that of Comparative Example 9, which is the raw material zeolite.

比較例の結果をイオン半径で整理し、第5図に示す、こ
の結果、イオン半径1.7 と1.9人の間(Caイオ
ンとSrイオンの間)にNz吸着量の最大値をもつもの
と考えられる。そこで、CaとSrの複合イオン、すな
わち1両イオンの混合比を変えることにより、N2吸着
量の増加を図った。
The results of the comparative example are organized by ionic radius and shown in Figure 5. As a result, the maximum value of the Nz adsorption amount is between the ionic radius of 1.7 and 1.9 (between Ca ions and Sr ions). considered to be a thing. Therefore, an attempt was made to increase the amount of N2 adsorption by changing the composite ion of Ca and Sr, that is, the mixing ratio of both ions.

最適なCaとSrの混合比を以下の実施例で決定した。The optimum mixing ratio of Ca and Sr was determined in the following example.

〈実施例1〉 直径1鵬、長さ5−の円柱状Na−A型ゼオライト15
0gを原料とし、硝酸カルシウム97gをIQの中に加
え攪拌しながら25℃で24時間含浸させた後、水洗し
、恒温槽で250℃、工時間焼成した試料を硝酸ストロ
ンチウム21gとともにIQの水に加えて攪拌しながら
25℃で24時間含浸させた後、水洗し、恒温槽で25
0℃、工時間焼成した試料を供試試料とし、吸着性能測
定方法によりNzの吸着容量を測定した。
<Example 1> Cylindrical Na-A type zeolite 15 with a diameter of 1 mm and a length of 5 mm
Using 0g of calcium nitrate as a raw material, add 97g of calcium nitrate to IQ and impregnate it at 25℃ for 24 hours with stirring, then wash with water and bake in a constant temperature bath at 250℃ for a working time.The sample was added to IQ water with 21g of strontium nitrate. After adding and impregnating at 25℃ for 24 hours with stirring, washing with water and soaking in a constant temperature bath for 25 hours.
A sample fired at 0° C. for a working time was used as a test sample, and the adsorption capacity of Nz was measured by an adsorption performance measuring method.

〈実施例2〉 直径1閣、長さ5■の円柱状Na−A型ゼオライト15
0gを原料とし、硝酸カルシウム97gをIQの中に加
え攪拌しながら25℃で24時間含浸させた後、水洗し
、恒温槽で250℃、工時間焼成した試料を硝酸ストロ
ンチウム42gとともにIQの水に加えて攪拌しながら
25℃で24時間含浸させた後、水洗し、恒温槽で25
0℃、工時間焼成した試料を供試試料とし、前記測定法
によりN2の吸着容量を測定した。
<Example 2> Cylindrical Na-A type zeolite 15 with a diameter of 1 cm and a length of 5 cm
Using 0g of calcium nitrate as a raw material, add 97g of calcium nitrate to IQ and impregnate it at 25℃ for 24 hours with stirring, wash with water, and bake in a constant temperature bath at 250℃ for a working time.The sample was added to IQ water with 42g of strontium nitrate. After adding and impregnating at 25℃ for 24 hours with stirring, washing with water and soaking in a constant temperature bath for 25 hours.
A sample fired at 0° C. for a working time was used as a test sample, and the N 2 adsorption capacity was measured using the measurement method described above.

〈実施例3〉 直径1■、長さ5■の円柱状Na−A型ゼオライト15
0g’S−原料とし、硝酸カルシウム97gをIQの水
に加え攪拌しながら25℃で24時間含浸させた後、水
洗し、恒温槽で250℃、工時間焼成した試料を硝酸ス
トロンチウム63gとともにIQの水に加えて攪拌しな
がら25℃で24時間含浸させた後、水洗し、恒温槽で
250℃、工時間焼成した試料を供試試料とし、前述の
測定法によりNzの吸着容量を測定した、。
<Example 3> Cylindrical Na-A type zeolite 15 with a diameter of 1 cm and a length of 5 cm
0g'S- raw material, 97g of calcium nitrate was added to IQ's water and impregnated with stirring at 25℃ for 24 hours, washed with water, and baked in a constant temperature bath at 250℃ for a processing time. The sample was impregnated with water and stirred at 25°C for 24 hours, washed with water, and baked in a constant temperature bath at 250°C for a working time, and the Nz adsorption capacity was measured using the above-mentioned measurement method. .

実施例1ないし3、さらに、比較例2と3を第2表及び
第6図に示した。
Examples 1 to 3 and Comparative Examples 2 and 3 are shown in Table 2 and FIG. 6.

第2表 この結果、Sr含有率が0〜65wt%、好ましくは1
0〜40wt%におけるN2吸着容量が大きいことが分
った。特に実施例1、すなわち。
Table 2 As a result, the Sr content is 0 to 65 wt%, preferably 1
It was found that the N2 adsorption capacity at 0 to 40 wt% was large. Especially in Example 1, ie.

Sr含有率25wt%でのN2吸着容量が最大値6.5
Ncc/gとなることが分った。
Maximum N2 adsorption capacity at 25wt% Sr content is 6.5
It was found that Ncc/g.

Sr以外のイオン、すなわちBa、Li、Mn。Ions other than Sr, namely Ba, Li, and Mn.

Ni、Crの金属イオンとCaを交換した複合イオン吸
着剤を製作し、N2吸着容量について、比較例10から
比較例16で明らかにした。
A composite ion adsorbent in which Ca was exchanged with metal ions of Ni and Cr was manufactured, and the N2 adsorption capacity was clarified in Comparative Examples 10 to 16.

く比較例10〉 直径11.長さ5■の円柱状Na−A型ゼオライト15
0gを原料とし、硝酸カルシウム48g。
Comparative Example 10> Diameter 11. Cylindrical Na-A type zeolite 15 with a length of 5 cm
0g as raw material, 48g of calcium nitrate.

及び、硝酸バリウム20gを1aの水に加えて攪拌しな
がら25℃で24時間含浸させた後、水洗し、恒温槽で
250℃、工時間焼成した試料を供試試料とし、吸着性
能測定方法によりN2の吸着容量を測定した。
Then, 20 g of barium nitrate was added to 1a of water and impregnated with stirring at 25°C for 24 hours, then washed with water and baked at 250°C in a constant temperature bath for a working time. The N2 adsorption capacity was measured.

く比較例11〉 Na−A型ゼオライト150gに硝酸カルシウム48g
及び硝酸リチウム13gを加えて実施例10と同様な方
法で供試試料を作成し、さらに、N2の吸着容量を測定
した。
Comparative Example 11> 48 g of calcium nitrate in 150 g of Na-A zeolite
A test sample was prepared in the same manner as in Example 10 by adding 13 g of lithium nitrate, and the N2 adsorption capacity was measured.

く比較例12〉 N a −A型ゼオライト150gに硝酸カルシウム4
8g及び硝酸マンガン18gを加えて実施例10と同様
な方法で供試試料を作成し、さらにNzの吸着容量を測
定した。
Comparative Example 12> Calcium nitrate 4 was added to 150 g of Na-A type zeolite.
A test sample was prepared in the same manner as in Example 10 by adding 8 g of manganese nitrate and 18 g of manganese nitrate, and the adsorption capacity of Nz was also measured.

〈比較例13〉 Na−A型ゼオライト150gに硝酸カルシウム48g
及び硝酸ニッケル13gを加えて実施例10と同様な方
法で供試試料を作成し、さらに、N2の吸着容量を測定
した。
<Comparative Example 13> 48 g of calcium nitrate in 150 g of Na-A zeolite
A test sample was prepared in the same manner as in Example 10 by adding 13 g of nickel nitrate, and the N2 adsorption capacity was measured.

〈比較例14〉 Na−A型ゼオライト150gに硝酸カルシウム48g
及び硝酸クロム17gを加えて実施例10と同様な方法
で供試試料を作成し、さらに、N2の吸着容量を測定し
た。
<Comparative Example 14> 48 g of calcium nitrate in 150 g of Na-A zeolite
A test sample was prepared in the same manner as in Example 10 by adding 17 g of chromium nitrate, and the N2 adsorption capacity was measured.

〈比較例15〉 Na−A型ゼオライト150gに硝酸カルシウム48g
及び硝酸マグネシウム18gを加えて実施例10と同様
な方法で供試試料を作成し、さらにNZの吸着容量を測
定した。
<Comparative Example 15> 48 g of calcium nitrate in 150 g of Na-A zeolite
A test sample was prepared in the same manner as in Example 10 by adding 18 g of magnesium nitrate, and the adsorption capacity of NZ was further measured.

比較例10〜15の結果を第3表に示す。The results of Comparative Examples 10 to 15 are shown in Table 3.

第3表 カルシウムとストロンチウムの複合イオンの場合に窒素
吸着容量6.5Ncc/g  となり、単一イオン交換
で最も性能の良かったカルシウム交換剤に比べて、窒素
吸着容量で35%、改善できた。
Table 3 In the case of composite ions of calcium and strontium, the nitrogen adsorption capacity was 6.5 Ncc/g, which was a 35% improvement in nitrogen adsorption capacity compared to the calcium exchanger that had the best performance in single ion exchange.

上記以外の複合イオンの組合わせでは、カルシウム交換
剤に比べてN2吸着容量が小さい。
Combinations of complex ions other than those listed above have a smaller N2 adsorption capacity than calcium exchangers.

原料ゼオライトとして適するものを下記の実施例により
選定した。
A suitable raw material zeolite was selected according to the following example.

〈実施例16) 直径lam、長さ5mの円柱状Na−A型ゼオライト1
50gを原料とし、硝酸カルシウム97g及びストロン
チウム21gをIQの水に加えて攪拌しながら25℃で
24時間含浸させた後、水洗し、恒温槽で250℃、工
時間焼成した試料を供試試料とし前述の測定法によりN
2の吸着容量を測定した。
<Example 16) Cylindrical Na-A type zeolite 1 with a diameter lam and a length of 5 m
Using 50g of raw material, 97g of calcium nitrate and 21g of strontium were added to IQ water and impregnated at 25℃ for 24 hours with stirring, then washed with water and baked at 250℃ in a constant temperature bath for a working time.The sample was used as a test sample. By the measurement method described above, N
The adsorption capacity of 2 was measured.

〈実施例17〉 原料にNa−X型ゼオライトを用い、他の操作は実施例
1と同じ。
<Example 17> The other operations were the same as in Example 1, using Na-X type zeolite as the raw material.

〈実施例18〉 原料にNa−Y型ゼオライトを用い、他の操作は実施例
16と同様である。
<Example 18> The other operations were the same as in Example 16, using Na-Y type zeolite as the raw material.

〈実施例19〉 原料にNa−L型ゼオライトを用い、他の操作は実施例
16と同様である。
<Example 19> Na-L type zeolite was used as the raw material, and the other operations were the same as in Example 16.

〈実施例20〉 原料にオフレタイト(Offretite)を用い、他
の操作は実施例16と同様である。
<Example 20> Offretite was used as the raw material, and the other operations were the same as in Example 16.

〈実施例21〉 原料にエリオナイト(Erionite)を用い、他の
操作は実施例16と同様である。
<Example 21> Erionite was used as the raw material, and the other operations were the same as in Example 16.

〈実施例22〉 原料にモルデナイト(Mordenita)を用い、他
の操作は実施例16と同様である。
<Example 22> Mordenite was used as the raw material, and the other operations were the same as in Example 16.

〈実施例23〉 原料にフェライト(Ferrierite)を用い、他
の操作は実施例16と同様である。
<Example 23> Ferrite was used as the raw material, and the other operations were the same as in Example 16.

〈実施例24〉 原料にZSM−5を用い、他の操作は実施例16と同様
である。
<Example 24> ZSM-5 was used as the raw material, and the other operations were the same as in Example 16.

実施例16〜24の結果を第4表に示す。The results of Examples 16 to 24 are shown in Table 4.

第4表 この中で、実施例16.17及び22のN2吸着容量が
高いことから、原料ゼオライトにはA型。
Table 4 Among these, Examples 16, 17 and 22 have high N2 adsorption capacities, so the raw material zeolite is type A.

X型及びモルデナイト(Mordenite)が適して
おり。
Type X and Mordenite are suitable.

特にA型が最適である。In particular, type A is most suitable.

〈実施例25〉 実施例1で得られたストロンチウムイオン交換率25w
t%の吸着剤を用いて圧力スイング吸着させた。その内
容について第1図を用いて以下に説明する。
<Example 25> Strontium ion exchange rate 25w obtained in Example 1
Pressure swing adsorption was performed using t% adsorbent. The contents will be explained below using FIG.

吸着剤2Qを充填した二個の吸着塔13A。Two adsorption towers 13A filled with adsorbent 2Q.

13Bにはそれぞれ原料ガス送入切り替え用の弁11A
、IIB、減圧時脱着ガス抜出し切り替え用の弁12A
、12B、製品ガス送り出し切り替え用の弁15A、1
5B、バッファタンク32からのガス送入切り替え用の
弁16A、16Bを備えている。原料ガス21は圧縮機
30により吸着圧力まで加圧された後、弁11で選択さ
れた吸着塔13に供給される。吸着工程で分離濃縮され
たガスは弁15で選択された吸着塔13から取り出され
製品タンク32に一時的に貯えられ、大部分が製品ガス
22として系外に取り出される。製品タンク32に貯え
られたガスの残部は弁16で選択された吸着塔13に送
られ、常圧パージ、予備加圧に使用される。脱着ガスに
関しては、大気圧開放時は弁12で選択された吸着塔1
3から脱着ガス23が大気に放出され、減圧時は弁12
で選・択された吸着塔13から真空ポンプ31で吸引さ
れた脱着ガス23が大気に放出される。
13B each has a valve 11A for switching raw material gas supply.
, IIB, valve 12A for switching desorption gas extraction during depressurization
, 12B, product gas delivery switching valve 15A, 1
5B, and valves 16A and 16B for switching gas supply from the buffer tank 32. After the raw material gas 21 is pressurized to adsorption pressure by the compressor 30, it is supplied to the adsorption tower 13 selected by the valve 11. The gas separated and concentrated in the adsorption process is taken out from the adsorption tower 13 selected by the valve 15 and temporarily stored in the product tank 32, and most of it is taken out of the system as the product gas 22. The remainder of the gas stored in the product tank 32 is sent to the adsorption tower 13 selected by the valve 16 and used for normal pressure purge and preliminary pressurization. Regarding the desorption gas, when the atmospheric pressure is released, the adsorption tower 1 selected by the valve 12
Desorption gas 23 is released to the atmosphere from 3, and when the pressure is reduced, the valve 12
The desorption gas 23 sucked by the vacuum pump 31 from the selected adsorption tower 13 is released to the atmosphere.

二個の吸着塔11A、11Bは経時的に吸着と再生が繰
り返されるが、原料ガスから酸素を分離除去する場合を
例としてその内容を、更に、詳細に説明する。
Adsorption and regeneration are repeated over time in the two adsorption towers 11A and 11B, and the contents thereof will be explained in more detail by taking as an example the case where oxygen is separated and removed from the raw material gas.

吸着塔13Aに原料ガスを供給する工程を工程Iとし、
以下連続する工程を順を追って説明する。
The step of supplying the raw material gas to the adsorption tower 13A is referred to as step I,
The successive steps will be explained in order below.

工程Iでは、 圧縮機30で1.5気圧に加圧された原料ガスが弁11
Aを通り吸着塔13Aに供給され、酸素フリーガスとし
て弁15Aを通り製品タンク32に貯蔵される。この間
に、吸着塔13Bは弁12Bを開いたまま、真空ポンプ
31により減圧排気される。工程■では、 吸着塔13Aは弁12Aを開いたまま、真空ポンプ31
により減圧排気される。
In process I, the raw material gas pressurized to 1.5 atmospheres by the compressor 30 is passed through the valve 11.
A, the gas is supplied to the adsorption tower 13A, and is stored as an oxygen-free gas in the product tank 32 through the valve 15A. During this time, the adsorption tower 13B is evacuated under reduced pressure by the vacuum pump 31 while the valve 12B is kept open. In step (2), the vacuum pump 31 of the adsorption tower 13A remains open with the valve 12A open.
It is decompressed and exhausted.

この間に、圧縮機30で1.5ataに加圧された原料
ガスが弁11Bを通り吸着塔13Bに供給され、精製ガ
スとして弁15Bを通り製品タンク32に貯蔵される。
During this time, the raw material gas pressurized to 1.5 ata by the compressor 30 is supplied to the adsorption tower 13B through the valve 11B, and is stored in the product tank 32 through the valve 15B as purified gas.

工程■完了後は、再び、工程■に戻る。After completing process ■, return to process ■ again.

弁の開閉シーケンスは第4表の通りとなる。The opening/closing sequence of the valves is as shown in Table 4.

第4表 0・・・弁開 X・・・弁閉 第4図に示す圧力スイング吸着装置を、第5表の操作手
順によって運転した。
Table 4 0...Valve open X...Valve closed The pressure swing adsorption apparatus shown in FIG. 4 was operated according to the operating procedure shown in Table 5.

第5表 操作条件は、吸着塔容積2Ωが2基、吸着圧力1.5a
ta、再生圧力0.34ata、サイクル時間120s
とした。
The operating conditions in Table 5 are two adsorption towers with a capacity of 2Ω and an adsorption pressure of 1.5a.
ta, regeneration pressure 0.34ata, cycle time 120s
And so.

く比較例16〉 実施例1で得られたカルシウムイオン交換吸着剤を用い
て圧力スイング吸着させた。操作方法は、実施例25と
同様とする。
Comparative Example 16> Pressure swing adsorption was carried out using the calcium ion exchange adsorbent obtained in Example 1. The operating method is the same as in Example 25.

実施例25、及び、比較例16の運転結果を第5表に示
す。この結果、実施例25及び比較例16における製品
酸素濃度90VoQ%時の酸素収率は58及び48%、
吸着剤使用量は80及び100 kg/ N rd O
x/ h  となる、従って、カルシウムにストロンチ
ウムを加えることによって酸素収率において21%増加
、吸着剤使用量は、25%低減できることが分った。
The operation results of Example 25 and Comparative Example 16 are shown in Table 5. As a result, the oxygen yields in Example 25 and Comparative Example 16 when the product oxygen concentration was 90 VoQ% were 58% and 48%,
The amount of adsorbent used is 80 and 100 kg/Nrd O
x/h. Therefore, it was found that by adding strontium to calcium, the oxygen yield could be increased by 21% and the amount of adsorbent used could be reduced by 25%.

本発明による吸着剤を用いた酸素濃縮装置を自動車用エ
ンジンに適用する場合の構成図を第2図に示す。エンジ
ンの混合器のように被供給装置51から供給されたガス
をPSA酸素濃縮装置52に導いて、酸素富化ガスを生
成し、−そのガスを自動車用エンジンに導びいてエンジ
ンの燃焼効率を高めることができる。PSA酸素濃縮装
置52として1本発明の吸着剤を第3図の装置により、
第5表のシーケンスを行なわせることにより、吸着剤量
の低減、及び、PSA装置の小型化が図れることから、
自動車への適用が可能となる。
FIG. 2 shows a configuration diagram when the oxygen concentrator using the adsorbent according to the present invention is applied to an automobile engine. Gas supplied from a supplied device 51, such as an engine mixer, is directed to a PSA oxygen concentrator 52 to produce an oxygen-enriched gas, and the gas is directed to an automotive engine to improve engine combustion efficiency. can be increased. As a PSA oxygen concentrator 52, the adsorbent of the present invention is used in the apparatus shown in FIG.
By performing the sequence shown in Table 5, it is possible to reduce the amount of adsorbent and downsize the PSA device.
Application to automobiles becomes possible.

また1本発明は医療用にも良好に適用できる。Furthermore, the present invention can be favorably applied to medical applications.

従来のPSAでは装置が大きく、可搬性に難があったが
1本発明により、小型・軽量の酸素濃縮装置が可能にな
る。
Conventional PSA devices are large and have difficulty in portability, but the present invention enables a small and lightweight oxygen concentrator device.

さらに、本発明は微生物の培養にも適用できる。Furthermore, the present invention can also be applied to culturing microorganisms.

すなわち、微生物は成長に伴って酸素を消費するが、成
長速度に応じて酸素を供給できれば増殖効率が高くなる
0本発明によれば、酸素濃縮装置の小型化が図れること
から、微生物培養への適用が可能となる。
In other words, microorganisms consume oxygen as they grow, but if oxygen can be supplied according to the growth rate, the growth efficiency will be increased.According to the present invention, since the oxygen concentrator can be made smaller, Application becomes possible.

さらに、本発明の吸着方法による酸素濃縮装置を石炭ガ
ス化複合発電(通称IGCC)に適用した場合の構成図
を第3図に示す。この吸着方法による酸素濃縮装置81
によって製造した酸素に富むガスをガス化炉82に導び
き燃焼させることによって発生する蒸気をタービン83
に供給して発電するシステムである。本吸着方法により
、ガス化炉の燃焼効率が向上するため、IGCC全体の
複合発電効率も向上する。
Further, FIG. 3 shows a configuration diagram when the oxygen concentrator using the adsorption method of the present invention is applied to coal gasification combined cycle power generation (commonly known as IGCC). Oxygen concentrator 81 using this adsorption method
The oxygen-rich gas produced by
This is a system that supplies electricity to generate electricity. By this adsorption method, the combustion efficiency of the gasifier is improved, so the combined power generation efficiency of the entire IGCC is also improved.

酸素吹きIGCCを実用化するには、低価格の酸素を多
量に製造しうろことが不可欠となる。本吸着方法によれ
ば、酸素濃縮装置が小型化でき。
In order to put oxygen-blown IGCC into practical use, it is essential to produce large amounts of low-cost oxygen. According to this adsorption method, the oxygen concentrator can be downsized.

装置コストが低減できることからIGCCへの適用が可
能となる。
Since the device cost can be reduced, it can be applied to IGCC.

〔発明の効果〕〔Effect of the invention〕

本発明によれば、ゼオライトのNz吸着容量を約25%
増加できるので、吸着剤の使用量が25%少なくてすむ
ため、吸着剤の使用装置コストの大幅な低減が図れる。
According to the present invention, the Nz adsorption capacity of zeolite can be reduced by about 25%.
Since the amount of adsorbent used can be reduced by 25%, the cost of equipment for using the adsorbent can be significantly reduced.

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

第1図は本発明の一実施例の酸素濃縮装置の系統図、第
2図は本発明の応用例のブロック図、第3図は本発明の
他の応用例のブロック図、第4図は本発明の改質剤の評
価系統図、第5図は結合半径とNz@看容量との関係を
示す図、第6図はイオン半径とN2吸着容量との関係を
示す図である91・・・真空ポンプ、2・・・ベッセル
A、3・・・ベッセルB、4・・・温度調節器、5・・
・吸着剤、6・・・圧力セン第 図 第6図 Qlρ吟 イ万 二交碩牛 0す 5P勿1y /、0 7.5 結8−半糧(A)
Fig. 1 is a system diagram of an oxygen concentrator according to an embodiment of the present invention, Fig. 2 is a block diagram of an applied example of the present invention, Fig. 3 is a block diagram of another applied example of the present invention, and Fig. 4 is a system diagram of an oxygen concentrator according to an embodiment of the present invention. Evaluation system diagram of the modifier of the present invention, Figure 5 is a diagram showing the relationship between the bond radius and Nz @ absorption capacity, and Figure 6 is a diagram showing the relationship between the ionic radius and N2 adsorption capacity91...・Vacuum pump, 2... Vessel A, 3... Vessel B, 4... Temperature controller, 5...
・Adsorbent, 6...Pressure sensor Figure 6

Claims (1)

【特許請求の範囲】 1、シリカ及びアルミナを主成分とするゼオライトをカ
ルシウムとストロンチウムを含むカチオンでイオン交換
することを特徴とする酸素と窒素の分離吸着剤。 2、請求項1において、 ストロンチウムの含有量がカルシウムに対して0〜65
wt%、好ましくは10〜40wt%であることを特徴
とする酸素と窒素の分離吸着剤。 3、請求項1におけるゼオライトの結晶構造は、A型、
X型、Y型、L型、オフレタイト (Offretite)、エリオナイト(Erioni
te)、モルデナイト(Mordenite)、フェリ
ライト(Ferrierite)及びZSM−5から選
択されることを特徴とする酸素と窒素の分離吸着剤。 4、窒素を選択的に吸着する吸着剤を含有する吸着塔に
窒素及び酸素を含有する気体混合物を通過させて、酸素
に富むガスを製造し、前記吸着剤が窒素で飽和させた時
に、前記気体混合物の流れを停止し、前記吸着剤から窒
素に富むガスを除去する方法において、 前記吸着剤としてシリカ及びアルミナを主成分とするゼ
オライトをカルシウムとストロンチウムを含むカチオン
でイオン交換した吸着剤を用いることを特徴とする気体
混合物から窒素と酸素とを分離する吸着方法。 5、混合器のようなガス供給装置から排出された空気を
原料とし前記吸着方法による酸素濃縮装置によつて製造
した酸素に富むガスを自動車用エンジンに供給すること
を特徴とする請求項4に記載の応用装置。 6、前記吸着方法による酸素濃縮装置によつて製造した
酸素に富むガスをガス化炉に導びき燃焼させることによ
つて発生する蒸気をタービンに供給することを特徴とす
る請求項4に記載の応用装置。
[Claims] 1. An oxygen and nitrogen separation adsorbent characterized by ion-exchanging zeolite containing silica and alumina with cations containing calcium and strontium. 2. In claim 1, the content of strontium is 0 to 65 with respect to calcium.
An adsorbent for separating oxygen and nitrogen, characterized in that the content thereof is 10 to 40 wt%. 3. The crystal structure of the zeolite in claim 1 is type A,
X type, Y type, L type, Offretite, Erionite
TE), Mordenite, Ferrierite and ZSM-5. 4. Produce an oxygen-rich gas by passing a gas mixture containing nitrogen and oxygen through an adsorption column containing an adsorbent that selectively adsorbs nitrogen, and when the adsorbent is saturated with nitrogen, In the method of stopping the flow of the gas mixture and removing nitrogen-rich gas from the adsorbent, an adsorbent in which zeolite mainly composed of silica and alumina is ion-exchanged with cations containing calcium and strontium is used as the adsorbent. An adsorption method for separating nitrogen and oxygen from a gas mixture, characterized by: 5. According to claim 4, the oxygen-rich gas produced by the oxygen concentrator using the adsorption method using air discharged from a gas supply device such as a mixer as a raw material is supplied to the automobile engine. Application equipment as described. 6. The method according to claim 4, characterized in that the oxygen-rich gas produced by the oxygen concentrator using the adsorption method is introduced into a gasification furnace and combusted to supply steam generated by the turbine. Applied equipment.
JP1025800A 1989-02-06 1989-02-06 Oxygen and nitrogen separation adsorbent, adsorption method and application equipment Pending JPH02207838A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1025800A JPH02207838A (en) 1989-02-06 1989-02-06 Oxygen and nitrogen separation adsorbent, adsorption method and application equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1025800A JPH02207838A (en) 1989-02-06 1989-02-06 Oxygen and nitrogen separation adsorbent, adsorption method and application equipment

Publications (1)

Publication Number Publication Date
JPH02207838A true JPH02207838A (en) 1990-08-17

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP1025800A Pending JPH02207838A (en) 1989-02-06 1989-02-06 Oxygen and nitrogen separation adsorbent, adsorption method and application equipment

Country Status (1)

Country Link
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5616170A (en) * 1995-08-11 1997-04-01 The Boc Group, Inc. Adsorptive separation of nitrogen from other gases
JP2008505831A (en) * 2004-07-08 2008-02-28 ヒョスン・コーポレーション Purification method of nitrogen trifluoride gas using zeolite ion exchanged and impregnated with alkaline earth metal
JP2008505750A (en) * 2004-07-08 2008-02-28 ヒョスン・コーポレーション Purification method of nitrogen trifluoride gas using zeolite ion exchanged with alkaline earth metal

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5616170A (en) * 1995-08-11 1997-04-01 The Boc Group, Inc. Adsorptive separation of nitrogen from other gases
JP2008505831A (en) * 2004-07-08 2008-02-28 ヒョスン・コーポレーション Purification method of nitrogen trifluoride gas using zeolite ion exchanged and impregnated with alkaline earth metal
JP2008505750A (en) * 2004-07-08 2008-02-28 ヒョスン・コーポレーション Purification method of nitrogen trifluoride gas using zeolite ion exchanged with alkaline earth metal
US7842125B2 (en) 2004-07-08 2010-11-30 Hyosung Corporation Process for refining nitrogen trifluoride gas using alkali earth metal exchanged zeolite

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