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JPH0372007B2 - - Google Patents
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JPH0372007B2 - - Google Patents

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Publication number
JPH0372007B2
JPH0372007B2 JP59038690A JP3869084A JPH0372007B2 JP H0372007 B2 JPH0372007 B2 JP H0372007B2 JP 59038690 A JP59038690 A JP 59038690A JP 3869084 A JP3869084 A JP 3869084A JP H0372007 B2 JPH0372007 B2 JP H0372007B2
Authority
JP
Japan
Prior art keywords
adsorption
type zeolite
gas
zeolite
pressure
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
JP59038690A
Other languages
Japanese (ja)
Other versions
JPS60186410A (en
Inventor
Jun Izumi
Seiichi Shirakawa
Hiroyuki Tsutaya
Hiroyoshi Kawamura
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP59038690A priority Critical patent/JPS60186410A/en
Publication of JPS60186410A publication Critical patent/JPS60186410A/en
Publication of JPH0372007B2 publication Critical patent/JPH0372007B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/40Capture or disposal of greenhouse gases of CO2
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/151Reduction of greenhouse gas [GHG] emissions, e.g. CO2

Landscapes

  • Separation Of Gases By Adsorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Carbon And Carbon Compounds (AREA)

Description

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

本発明の対象 本発明はCO含有ガスからCOを吸着分離する方
法に関し、特に製鉄プラント、オートサーマル部
分酸化法、空気吹き石炭ガス化プラント等で生成
するCO,N2を含有する多成分ガスからのCO吸
着分離方法に関する。 従来技術の概要とその欠点 製鉄プラントのオフガス、天然ガス、液化石油
ガス、ナフサを原料とし空気を助燃剤とするオー
トサーマル部分酸化法、空気吹き石炭ガス化プラ
ントでは、CO,N2,H2O,H2等を主成分とする
ガスを生成する。 この混合ガスからのCOの選択的な濃縮は、CO
に各種用途があるので極めて有意義かつ重要であ
る。1つのCOの用途としては、CO,H2の混合
ガスからのメタノール合成の原料となる。他の用
途としてはCOはH2Oガスの共存下でシフト反応
によりH2を生成するのでH2源と見做す事もでき
る。又、他の用途としてはメタノールにCOを作
用させて酢酸を生成するカルボニル化法の原料と
しても考えられる。特に近年メタノールを原料と
するガソリン合成の実用化への展望が開かれつつ
あり、その意味でも重要である。 従来、COの分離は塩化アルミ銅(CuAlCl4
のトルエン溶液による液相吸収方法が最とも性能
が良いといわれている。この方法では、(1)式に示
すようなCOの吸収反応で塩化アルミ銅との等モ
ル吸収を起す。 CuAlCl4+COCuAlCl4・CO (1) 通常、室温付近で上記(1)式の吸収反応により上
記吸収液にCOを吸収せしめ、100℃以上の高温で
一度吸収したCOを離脱せしめて回収する方法で
ある。この方法におけるCOの吸収容量は圧力が
高い程増加するのでイニシヤルコストの低減の為
に数ataのやや高圧を採用する場合もある。又、
この方法では、COと随伴するガスが殆どない為、
得られるCOガスの濃度は99%程度と極めて高く、
かつ回収率も高い。 なお、この方法以外に銅液洗浄法、深冷分離法
等がCO濃縮方法があるが、上記液相吸収方法が
装置価格、動力費、得られるCO濃度のいずれで
も優れている事から主流になりつつある。 しかし、塩化アルミ銅のトルエン溶液による
COの吸収分離方法に於ける最大の欠点は、誤操
作等によつて混入するH2O,H2S,SO2等と
CuAlCl4が反応して、CuCl,HCl,CuAlCl6
(OH)等に分解し、塩化アルミ銅の減耗を生ず
ると共に、回収したCOにHClが随伴して製品の
品位を著しく減ずることである。 次に挙げられる欠点は、オレフイン、アセチレ
ンがCuAlCl4と反応して沈澱を生成することであ
り、この反応は不可逆である為、CuAlCl4のメー
クアツプが必要であることである。又溶媒として
トルエンを使用している事から、オフガス及び
CO回収(ストリツパー)ユニツトのいずれにも
トルエンが随伴する事から活性炭を吸着剤として
使用して水蒸気を再生ガスとするトルエン回収ユ
ニツトが必要であることであり、当然の事ながら
トルエンのメークアツプも必要となる欠点があ
る。 この方法は、動力費としては、吸収工程を大気
圧近くで操作する事も可能であり、電力消費は少
ないという長所もあるが、トルエン回収ユニツト
の再生用水蒸気、CO回収ユニツトの回収用熱源
としての水蒸気が必要であり、この水蒸気発生の
ための熱量は、電力換算で上記消費電力の2〜3
倍に相当し、結局消費電力は大で経済的ではな
い。 本発明の目的 本発明はCO,N2等を主として含有する混合ガ
スからCOのみを選択的に比較的低圧で(大気圧
以上の)吸着し、これを0.5ata以下の減圧条件で
回収する事による、極めて簡単なプロセスにより
殆ど化学薬品のメークアツプをせず、又保守操作
の容易なCOの回収方法の提供を目的とする。 本発明の新しい点 本発明は、COの選択吸着剤として、Na−A型
ゼオライト又はNa−A型ゼオライトに2価又は
3価のFeを含浸し、これを熱処理したA型ゼオ
ライトを吸着剤として使用することを新規とする
ものである。これら吸着剤は、N2,O2の2成分
系からの分離例等から判断して吸着窓径は3.8〜
4.0Åと推定される。 なおこゝでいうNa−A型ゼオライトとは以下
に述べるものを云う。 化学式Mk/n・(AlO2)k・SiO2(こゝでMは
交換可能な金属イオン、nはその価数、Kは
AlO2/SiO2比である)で表わされ、通常結晶水
を有し、加熱脱気により結晶構造を変化すること
なく結晶水が離脱してガスの吸着能が出現するア
ルミニノシリケートにおいて、MがNaイオン、
K=1、n=1のものをNa−A型ゼオライトと
いう。 なお後記のNa−X型ゼオライトとは、MがNa
イオン、K=0.67〜0.83、n=1のものをいう。 この吸着剤を少くとも2塔以上の吸着塔に充填
し、吸着塔の温度は−30℃以上25℃(室温)以下
として、1塔にCO,N2を含有するガスを1〜
5ataで流過してCOを吸着せしめ、又他塔では前
に吸着したCOを0.05ataから0.5ataの減圧してN2
の共吸着を抑制しつつ高濃度にCOを回収するこ
とも新規な点とするものである。 更に回収したCOの一部を吸着工程終了直後の
吸着塔に吸着工程と同じガス流れ方向に流下して
塔内に残存するN2を掃気して、減圧再生時に回
収されるCOの濃度を向上させることもできる。 すなわち本発明は、Na−A型ゼオライトにバ
インダを混合して成形後熱処理してなるA型ゼオ
ライト、Na−A型ゼオライト(Naの18モル%ま
でK置換したものを含む)にFeイオンを含浸さ
せ、バインダを混合して成形後、熱処理してなる
A型ゼオライト、及びNa−A型ゼオライトにFe
イオンを含浸させ、Naの18モル%までK置換し、
バインダを混合して成形後、熱処理してなるA型
ゼオライトよりなる群から選らばれたA型ゼオラ
イトを、CO吸収剤として充填した少なくとも2
塔以上の吸着塔に、CO,N2などを主として含有
する混合ガスを導き、吸着圧力1〜5ata、吸着温
度室温〜−30℃の操作条件でCO吸着を行わせた
後、脱着圧力0.05〜0.5ataの操作条件でCO脱着さ
せることを特徴とするCO吸着分離方法に関する
ものである。 本発明の応用分野 本発明は、H2製造工業、メタノール工業、酢
酸工業、合成ガソリン工業(C1化学工業)に有
利に適用することができ、オフガス、プロセスガ
ス等ボイラ燃料の発熱量向上にも役立てせること
ができる。 本発明の具体例の説明 以下、本発明の具体的実施態様を、第1図を参
照しながら説明する。 第1図において、1はプロパンを原料とし、助
燃剤として酸素富化空気を使用した部分酸化法に
よるCO,H2合成ガス製造装置である。該CO,
H2合成ガス製造装置1内のガス組成の1例を表
−1に示す。
Object of the present invention The present invention relates to a method for adsorbing and separating CO from CO-containing gases, and in particular from multicomponent gases containing CO and N 2 produced in steel plants, autothermal partial oxidation methods, air-blown coal gasification plants, etc. This paper relates to a CO adsorption separation method. Overview of conventional technology and its drawbacks Autothermal partial oxidation method using off-gas from steel plants, natural gas, liquefied petroleum gas, and naphtha as raw materials and air as a combustion improver, and air-blown coal gasification plants use CO, N 2 , H 2 Generates gas whose main components are O, H2, etc. Selective enrichment of CO from this gas mixture is CO
It is extremely meaningful and important because it has various uses. One use of CO is as a raw material for methanol synthesis from a mixed gas of CO and H 2 . For other uses, CO can be regarded as an H 2 source since it generates H 2 through a shift reaction in the coexistence of H 2 O gas. Another possible use is as a raw material for a carbonylation method in which acetic acid is produced by reacting CO with methanol. Particularly in recent years, prospects for the practical application of gasoline synthesis using methanol as a raw material are opening up, and this is important in that sense as well. Conventionally, CO is separated using copper aluminum chloride (CuAlCl 4 ).
The liquid phase absorption method using a toluene solution is said to have the best performance. In this method, the absorption reaction of CO as shown in equation (1) causes equimolar absorption with copper aluminum chloride. CuAlCl 4 +COCuAlCl 4・CO (1) Usually, CO is absorbed into the above absorption liquid through the absorption reaction of equation (1) above at around room temperature, and the CO that has been absorbed is released and recovered at a high temperature of 100°C or higher. be. In this method, the CO absorption capacity increases as the pressure increases, so a slightly higher pressure of several ata may be used to reduce the initial cost. or,
With this method, there is almost no CO and accompanying gas, so
The concentration of CO gas obtained is extremely high, around 99%.
And the recovery rate is also high. In addition to this method, there are CO concentration methods such as copper liquid cleaning method and cryogenic separation method, but the liquid phase absorption method mentioned above has become mainstream because it is superior in terms of equipment cost, power cost, and CO concentration obtained. It is becoming. However, due to toluene solution of aluminum copper chloride
The biggest drawback in the CO absorption and separation method is that H 2 O, H 2 S, SO 2, etc. that get mixed in due to incorrect operation etc.
CuAlCl 4 reacts to form CuCl, HCl, CuAlCl 6
It decomposes into (OH), etc., causing depletion of aluminum copper chloride, and the recovered CO is accompanied by HCl, significantly reducing the quality of the product. The next drawback is that olefin and acetylene react with CuAlCl 4 to form a precipitate, and this reaction is irreversible, so make-up of CuAlCl 4 is required. Also, since toluene is used as a solvent, off-gas and
Since toluene accompanies all CO recovery (stripper) units, a toluene recovery unit that uses activated carbon as an adsorbent and uses water vapor as regeneration gas is required, and of course, toluene make-up is also required. There is a drawback. In terms of power costs, this method has the advantage of being able to operate the absorption process at near atmospheric pressure and consumes little electricity; of water vapor is required, and the amount of heat to generate this water vapor is equivalent to 2 to 3 times the above power consumption in terms of electricity.
This is equivalent to double the power consumption, which is not economical as the power consumption is large. Purpose of the present invention The present invention is a method of selectively adsorbing only CO from a mixed gas mainly containing CO, N2 , etc. at relatively low pressure (above atmospheric pressure) and recovering it under reduced pressure conditions of 0.5 ata or less. The purpose of the present invention is to provide a CO recovery method that uses an extremely simple process, requires little chemical make-up, and is easy to maintain and operate. New features of the present invention The present invention uses Na-A type zeolite or Na-A type zeolite impregnated with divalent or trivalent Fe and heat-treating it as an adsorbent. It is new to use. Judging from separation examples from two-component systems of N 2 and O 2 , these adsorbents have adsorption window diameters of 3.8 to 3.8.
Estimated to be 4.0Å. The Na-A type zeolite referred to herein refers to the following. Chemical formula Mk/n・(AlO 2 )k・SiO 2 (where M is an exchangeable metal ion, n is its valence, and K is
In aluminosilicate, which is expressed by the ratio AlO 2 /SiO 2 ), it usually has water of crystallization, and when heated and degassed, the water of crystallization is released without changing the crystal structure and gas adsorption ability appears. M is Na ion,
A zeolite with K=1 and n=1 is called Na-A type zeolite. Note that the Na-X type zeolite mentioned later refers to M as Na-X type zeolite.
ion, K=0.67-0.83, n=1. This adsorbent is packed into at least two or more adsorption towers, and the temperature of the adsorption tower is set at -30°C or higher and 25°C or lower (room temperature), and one to two gases containing CO and N2 are packed into each tower.
5 ata to adsorb CO, and in another column, the previously adsorbed CO is reduced to 0.05 ata to 0.5 ata to become N2.
Another novel feature is the ability to recover CO at a high concentration while suppressing the co-adsorption of CO. Furthermore, a portion of the recovered CO flows down into the adsorption tower immediately after the adsorption process is completed in the same gas flow direction as the adsorption process to scavenge the remaining N 2 in the tower and improve the concentration of CO recovered during reduced pressure regeneration. You can also do so. That is, the present invention is an A-type zeolite obtained by mixing a binder with Na-A-type zeolite and heat-treating the mixture after molding, and a Na-A-type zeolite (including one in which up to 18 mol% of Na is substituted with K) is impregnated with Fe ions. A-type zeolite and Na-A-type zeolite are produced by mixing a binder, molding, and heat treatment.
Impregnated with ions and substituted with K up to 18 mol% of Na.
At least two types of A-type zeolite selected from the group consisting of A-type zeolite formed by mixing a binder, molding, and heat treatment are filled as a CO absorbent.
A mixed gas mainly containing CO, N2 , etc. is introduced into an adsorption tower above the tower, and CO adsorption is performed under operating conditions of an adsorption pressure of 1 to 5 ata and an adsorption temperature of room temperature to -30°C, followed by a desorption pressure of 0.05 to -30°C. This invention relates to a CO adsorption separation method characterized by CO desorption under operating conditions of 0.5ata. Field of application of the present invention The present invention can be advantageously applied to the H2 manufacturing industry, methanol industry, acetic acid industry, synthetic gasoline industry (C1 chemical industry), and can also be used to improve the calorific value of boiler fuel such as off gas and process gas. You can make it useful. Description of Specific Examples of the Present Invention Hereinafter, specific embodiments of the present invention will be described with reference to FIG. In FIG. 1, reference numeral 1 indicates a CO, H 2 synthesis gas production apparatus using propane as a raw material and a partial oxidation method using oxygen-enriched air as a combustion improver. The CO,
Table 1 shows an example of the gas composition in the H 2 synthesis gas production apparatus 1.

【表】 CO,H2合成ガス製造装置1内の合成ガスは流
路2を通じて圧縮機3で加圧される。加圧された
合成ガスは、流路4を通じてバルブ5に至る。 この時バルブ5,6は開となつており、合成ガ
スは吸着塔8を流過する。吸着塔8及び8′では
入口側半分に活性アルミナが後方にはNa−X型
ゼオライトが充填されている。 その為、塔8の前方では、水が吸着され、後方
ではCO2が吸着される。一方、一度吸着された
H2O,CO2は、吸着塔8′の状態、即ち減圧脱着
工程にあり、バルブ7′が開いており、バルブ7,
6′が閉じている。バルブ7,7′に通じる流路9
は、他方を真空ポンプ10と通じている。吸着塔
8′は最高到達圧力は0.05ataに達し、H2O,CO2
を除去再生する。吸着塔8,8′を2〜10分程度
で交互に切り換えて連続的に除湿、CO2除去を行
なう。 除湿、CO2除去された合成ガスは、流路11、
サージタンク12を通じて、熱交換器13、冷凍
機14に至り、ガス温度は室温以下−60℃迄の任
意の温度に冷却されてバルブ15に至る。バルブ
15及び16は開状態となつている。流過する合
成ガスの流路11でのガス組成を表−2に示す。
[Table] The synthesis gas in the CO, H 2 synthesis gas production apparatus 1 is pressurized by the compressor 3 through the flow path 2. The pressurized synthesis gas passes through channel 4 to valve 5 . At this time, the valves 5 and 6 are open, and the synthesis gas flows through the adsorption tower 8. In the adsorption towers 8 and 8', the inlet half is filled with activated alumina, and the rear half is filled with Na-X type zeolite. Therefore, water is adsorbed at the front of the tower 8, and CO 2 is adsorbed at the rear. On the other hand, once adsorbed
H 2 O and CO 2 are in the state of the adsorption tower 8', that is, in the vacuum desorption process, and the valve 7' is open;
6' is closed. Channel 9 leading to valves 7, 7'
communicates with the vacuum pump 10 on the other side. The maximum pressure in the adsorption tower 8' reaches 0.05ata, and H 2 O, CO 2
Remove and play. The adsorption towers 8, 8' are switched alternately every 2 to 10 minutes to continuously dehumidify and remove CO2 . The dehumidified and CO 2- removed synthesis gas is passed through the flow path 11,
The gas passes through the surge tank 12 to a heat exchanger 13 and a refrigerator 14, where the gas temperature is cooled to an arbitrary temperature from room temperature to -60°C, and then reaches a valve 15. Valves 15 and 16 are in an open state. Table 2 shows the gas composition of the flowing synthesis gas in the channel 11.

【表】 CO吸着塔18を流過する合成ガスからCOは吸
着され、又CO吸着剤の選択性に応じてN2が共吸
着される。H2の吸着は無視し得る。 本実施例ではCO吸着塔18に下記の5種類を
充填して比較した。 Na−A型ゼオライト(ユニオンカーバイド
社製モレキユラーシーブス4A粉末)スラリー
にFe()Cl3を添加してNa−A型ゼオライト
にFe(OH)3,FeO・OH等Fe()水酸化物を
ゼオライトに対し1w%asFeで析出させる。 これを水洗ろ過した後、バインダーとしてカ
オリンを30w%混合して成形して、空気中で
700℃1時間焼成したもの。 O2,N22成分系からのO2吸着、N2共吸着に
関する別の試験によると窓径はNa−Aよりや
や小さい3.9〜3.95Åである。(試料A) 同上のNa−A型ゼオライトスラリーにFe
()Cl3を添加して、Na−A型ゼオライトに
Fe(OH)3,FeO・OH等Fe()水酸化物をゼ
オライトに対し1w%asFeで析出させかつNa−
A型ゼオライトのNaの5mol%をKで交換す
る。 これをろ過、水洗した後バインダーとしてカ
オリンを30w%混合して成形し空気中で700℃
3時間焼成したもの。 O2,N22成分系での吸着試験により窓径は更
に小さく3.8〜3.85Åである。(試料B) 同上のNa−A型ゼオライトにバインダーと
してカオリンを30w%混合して成形し、空気中
で650℃1時間焼成したもの。 窓径は4Å程度である。(試料C) 同上のNa−A型ゼオライトのNaの66mol%
を当量のCaで交換しバインダーとしてカオリ
ンを30w%混合成形し、空気中で650℃1時間
焼成したもの。 窓径は5Åである。(試料D) 同上のNa−A型ゼオライトのNaを全量Kで
交換し、バインダーとしてカオリンを30w%混
合成形し、空気中で650℃1時間焼成したもの。 窓径は3Åである。(試料E) CO吸着の終了した吸着塔18′は、バルブ1
5′,16′,17が閉じられ、バルブ17′が開
いており、流路19、熱交換器13′、真空ポン
プ20を通じて吸着塔18′の装着されたCOは減
圧状態で流路21から高い濃度に回収される。こ
の操作を1〜5分おきに交互にくり返す事により
高濃度のCOが連続して回収される。 熱交換器22は真空ポンプの後方の製品COの
温度が150℃程度に上昇するので、冷却のために
設置されている。 1方吸着塔18、バルブ16を通じて流路23
からCO濃度の低いガスが流過する。 なお、流路23の低COガスは高濃度にH2を含
む為、Na−X型ゼオライト、Ca置換Na−A型
ゼオライトなどN2吸着量の大きな吸着剤でN2
除去すると高濃度のH2が得られる。又深冷分離
法によりN2を液化して除去しても同様に高純度
のH2が得られる。又流路の23のガスは燃料と
して使用すれば、熱回収もできる。なお熱収支的
にみると、流路11のガスと流路19、流路23
のガスは熱交換器13,13′,13″でガス−ガ
ス熱交換をしている為、冷凍機14の消費電力は
極めて少ない。 本発明では、吸着塔18,18′及びその周囲
の配管、バルブをコールドボツクス24に設置し
て低温での吸着操作を行なつた。 以上の装置構成及びガス組成で、表−3の操作
を行ないCOの回収を試みた。
[Table] CO is adsorbed from the synthesis gas flowing through the CO adsorption tower 18, and N 2 is co-adsorbed depending on the selectivity of the CO adsorbent. Adsorption of H2 is negligible. In this example, the CO adsorption tower 18 was filled with the following five types for comparison. Fe()Cl 3 is added to Na-A type zeolite (Molecular Sieves 4A powder manufactured by Union Carbide) slurry, and Fe() hydroxides such as Fe(OH) 3 and FeO・OH are added to Na-A type zeolite. is precipitated with 1w% asFe on zeolite. After washing and filtering this with water, 30w% of kaolin is mixed as a binder, molded, and placed in the air.
Baked at 700℃ for 1 hour. According to another test regarding O 2 adsorption and N 2 co-adsorption from a two-component system of O 2 and N 2 , the window diameter is 3.9 to 3.95 Å, which is slightly smaller than that of Na-A. (Sample A) Fe was added to the same Na-A type zeolite slurry as above.
() Adding Cl3 to Na-A type zeolite
Fe(OH) hydroxides such as Fe(OH) 3 and FeO・OH are precipitated at 1w% asFe on zeolite, and Na−
5 mol% of Na in A-type zeolite is exchanged with K. After filtering and washing with water, 30w% of kaolin is mixed as a binder and molded at 700℃ in air.
Baked for 3 hours. Adsorption tests using a two-component system of O 2 and N 2 show that the window diameter is even smaller, ranging from 3.8 to 3.85 Å. (Sample B) The same Na-A zeolite as above was mixed with 30w% of kaolin as a binder, molded, and calcined in air at 650°C for 1 hour. The window diameter is about 4 Å. (Sample C) 66 mol% of Na in the same Na-A zeolite
was replaced with an equivalent amount of Ca, mixed with 30w% kaolin as a binder, and fired in air at 650℃ for 1 hour. The window diameter is 5 Å. (Sample D) The Na-A type zeolite mentioned above was completely replaced with K, and 30w% of kaolin was mixed and molded as a binder, and the mixture was calcined in air at 650°C for 1 hour. The window diameter is 3 Å. (Sample E) In the adsorption tower 18' where CO adsorption has been completed, valve 1
5', 16', and 17 are closed, and the valve 17' is open, and the CO installed in the adsorption tower 18' is discharged from the channel 21 under reduced pressure through the channel 19, the heat exchanger 13', and the vacuum pump 20. Collected at high concentration. By repeating this operation alternately every 1 to 5 minutes, high-concentration CO is continuously recovered. The heat exchanger 22 is installed to cool the product CO after the vacuum pump because the temperature rises to about 150°C. One-way adsorption tower 18, flow path 23 through valve 16
Gas with low CO concentration flows through. Note that the low CO gas in the flow path 23 contains H 2 at a high concentration, so if N 2 is removed using an adsorbent with a large amount of N 2 adsorption, such as Na-X zeolite or Ca-substituted Na-A zeolite, a high concentration of H 2 can be obtained. H2 is obtained. Furthermore, even if N 2 is liquefied and removed by cryogenic separation, highly pure H 2 can be obtained in the same way. Moreover, if the gas in the flow path 23 is used as fuel, heat can be recovered. In addition, from a heat balance perspective, the gas in the flow path 11, the flow path 19, and the flow path 23
Since the gas is subjected to gas-to-gas heat exchange in the heat exchangers 13, 13', 13'', the power consumption of the refrigerator 14 is extremely small. A valve was installed in the cold box 24 to perform adsorption operations at low temperatures. With the above equipment configuration and gas composition, CO recovery was attempted by performing the operations shown in Table 3.

【表】 上記の操作条件でのCOの回収結果を示す。 第2図は吸着温度0℃、脱着圧力0.1ataでの
CO回収時の各吸着剤の性能を、横軸に吸着圧力、
縦軸にCO濃度を選び示したものである。図中で
各試料のデータが判るように実測点を試料Aにつ
いては◎、試料Bについては○、試料Cについて
は△、試料Dについては□としている。なお、試
料E(K−A)は何らの吸着能も示さなかつた為
図から削除している。 第3図は吸着圧力1.2ata、吸着温度0℃での各
吸着剤のCOの回収性能を横軸に脱着圧力、縦軸
にCO濃度を選び示したものである。 図中の記号は第2図に等しい。 第4図は吸着圧力1.2ata、脱着圧力0.1ataでの
各吸着剤のCO回収性能を縦軸に吸着時の温度、
縦軸にCO濃度を選び示したものである。図中の
記号は第2図に等しい。 以上で判るように、Na−A型ゼオライト(資
料C)又はこれよりやや窓径の小さなA型ゼオラ
イト(試料A及びB)はCO,N2等からN2の吸着
を極力抑制しつつ高いCO選択性で回収し得る事
を示した。この事は、従来知られていない事であ
り、新しいCOの吸着分離方法を提供するもので
ある。 なお、K置換については資料Cのみしかあげて
いないが、Naの18モル%まで置換したものも
略々資料Cと同じ結果が得られた。またFe含浸
前にNa−A型ゼオライトのNaをK置換した資料
はあげていないが、K置換はFe含浸前後を問は
ず同じであつて、先ずNaの18モル%までをK置
換した後、Fe含浸したものも資料Cと略々同様
な結果が得られた。 なお本発明方法に於けるCOの回収率は原料の
CO濃度に大きく依存するが、原料CO濃度(流路
11でCO2,H2O除去後のもの)が50vol%の時
約90%前後である。 なおCOの回収率は CO回収率=製品CO流路21で単位時間に回
収されるCO量/入口流路11で単位時間に流入するCO量
×100% で定義している。 第3図に於いて再生圧力は絶対真空に近づく
程、回収CO濃度は上昇している。しかし0.05ata
以下では真空ポンプの消費電力が増大し又容量の
制限も受ける為工業的に有効とはいえない。 第4図に於いて−30℃以下の低温でも良好な
CO吸着性能を示している事が判る。 しかしながら−30℃以上であれば一元冷媒の1
段圧縮機で冷凍機は構成される。しかし、−30℃
以下になると冷媒が2種類以上必要であるとか圧
縮機が2段必要とかで設備的に大変である。又冷
凍時の消費電力も大幅に上昇する。 本発明の他の実施態様を第5図に示す。第5図
において第1図と同一符号は第1図と同じ部分を
示す。 第5図に示す如く、流路19、熱交換器13′
を通じて減圧条件で真空ポンプ20によつて吸着
塔18′から回収されたCOは熱交換器22を通じ
て流路21にとり出される。 この時吸着塔18に着目すると、吸着塔18の
前方には原料COガスが流入し塔の後方にいく程
N2濃度が上昇している。 前記実施態様(第1図)ではこの状態からCO
を回収した為塔のガイド部に残留するN2が随伴
しCOの濃度を低下せしめていた。 その為ここでは吸着工程終了直後に製品タンク
25のガスの一部を流路26、熱交換器13を
通じて開状態になつているバルブ27,15から
製品COを掃気する。 この為吸着塔18のボイド部の残留N2は開状
態のバルブ16、流路23、熱交換器13″を通
じて系外に放出される。 なお塔18のCO濃度が上昇する為ボイド部の
N2だけでなく共吸着したN2の一部も除去され
る。 なお製品COによるボイド部の掃気は製品とし
て回収したCOの10%程度で充分である。 本発明では試料A、B、Cについて、吸着圧力
1.2ata再生圧力0.1ata、塔温度0℃で製品COによ
る掃気を実施しいずれも99%以上の濃度のCOを
得る事ができた。 下記にバルブ操作の1例を示す。
[Table] Shows the CO recovery results under the above operating conditions. Figure 2 shows the adsorption temperature at 0℃ and desorption pressure at 0.1ata.
The performance of each adsorbent during CO recovery is plotted with adsorption pressure on the horizontal axis,
The vertical axis shows CO concentration. In order to understand the data for each sample in the figure, the actual measurement points are marked ◎ for sample A, ○ for sample B, △ for sample C, and □ for sample D. Note that sample E (K-A) did not show any adsorption ability and was therefore deleted from the diagram. Figure 3 shows the CO recovery performance of each adsorbent at an adsorption pressure of 1.2 ata and an adsorption temperature of 0°C, with the horizontal axis representing the desorption pressure and the vertical axis representing the CO concentration. The symbols in the figure are the same as in FIG. Figure 4 shows the CO recovery performance of each adsorbent at an adsorption pressure of 1.2 ata and a desorption pressure of 0.1 ata, with the temperature at adsorption plotted on the vertical axis.
The vertical axis shows CO concentration. The symbols in the figure are the same as in FIG. As can be seen from the above, Na-A type zeolite (Document C) or A type zeolite with a slightly smaller window diameter (Samples A and B) suppresses the adsorption of N2 from CO, N2, etc. as much as possible while reducing high CO2. It was shown that it can be recovered with selectivity. This has not been previously known and provides a new method for adsorption and separation of CO. Regarding K substitution, only Material C is listed, but almost the same results as Material C were obtained when Na was substituted up to 18 mol%. In addition, although there is no reference to K substitution for Na in Na-A type zeolite before Fe impregnation, K substitution is the same before and after Fe impregnation, and after first replacing up to 18 mol% of Na with K, Almost the same results as Material C were obtained for the material impregnated with Fe. Note that the CO recovery rate in the method of the present invention depends on the raw material.
Although it depends largely on the CO concentration, it is around 90% when the raw material CO concentration (after removing CO 2 and H 2 O in the flow path 11) is 50 vol%. Note that the CO recovery rate is defined as: CO recovery rate = amount of CO recovered per unit time in the product CO flow path 21 / amount of CO flowing in per unit time in the inlet flow path 11 x 100%. In Figure 3, the recovered CO concentration increases as the regeneration pressure approaches absolute vacuum. But 0.05ata
Below this, the power consumption of the vacuum pump increases and the capacity is limited, so it cannot be said to be industrially effective. In Figure 4, it shows good performance even at low temperatures below -30℃.
It can be seen that it shows CO adsorption performance. However, if it is above -30℃, the unitary refrigerant
The refrigerator consists of stage compressors. However, −30℃
Below this, it becomes difficult to use equipment because two or more types of refrigerants are required and two stages of compressors are required. Furthermore, the power consumption during refrigeration also increases significantly. Another embodiment of the invention is shown in FIG. In FIG. 5, the same reference numerals as in FIG. 1 indicate the same parts as in FIG. As shown in FIG. 5, the flow path 19 and the heat exchanger 13'
The CO recovered from the adsorption tower 18' by the vacuum pump 20 under reduced pressure conditions is taken out to the flow path 21 through the heat exchanger 22. At this time, focusing on the adsorption tower 18, the raw material CO gas flows into the front of the adsorption tower 18, and as it goes to the rear of the tower,
N2 concentration is rising. In the embodiment (Fig. 1), CO
Since the CO was recovered, the N 2 remaining in the guide section of the tower accompanied the CO and lowered the concentration of CO. Therefore, immediately after the adsorption process is completed, a part of the gas in the product tank 25 is passed through the flow path 26 and the heat exchanger 13, and the product CO is scavenged from the valves 27 and 15 which are in an open state. For this reason, the residual N 2 in the void part of the adsorption tower 18 is released to the outside of the system through the open valve 16, the flow path 23, and the heat exchanger 13''.
Not only N 2 but also part of the co-adsorbed N 2 is removed. Note that approximately 10% of the CO recovered as a product is sufficient for scavenging the void area with product CO. In the present invention, for samples A, B, and C, the adsorption pressure
Scavenging with product CO was carried out at a regeneration pressure of 1.2 ata, 0.1 ata, and a tower temperature of 0°C, and CO with a concentration of over 99% could be obtained in both cases. An example of valve operation is shown below.

【表】 本発明の他の具体的実施態様を以下に示す。 第5図と同一のフローシートに於いて、表−4
に示すガス組成の製鉄所転炉ガスの1部を分岐
し、940Nm3/hで分離濃縮した。その時の分離
条件及び結果を表−5に示す。
[Table] Other specific embodiments of the present invention are shown below. In the same flow sheet as Figure 5, Table-4
A part of the steelworks converter gas having the gas composition shown in was branched and separated and concentrated at 940Nm 3 /h. The separation conditions and results are shown in Table 5.

【表】【table】

【表】【table】

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

第1図は本発明の一実施態様を説明するフロ
ー、第2図は吸着温度0℃、脱着圧力0.1ataでの
CO回収時の各種吸着剤の性能を、横軸に吸着圧
力、縦軸にCO濃度を選んで示したグラフ、第3
図は吸着温度0℃での各種吸着剤のCOの回収性
能を横軸に脱着圧力、縦軸にCO濃度を選んで示
したグラフ、第4図は吸着圧力1.2ata、脱着圧力
0.1ataでの各種吸着剤のCO回収性能を、横軸に
吸着時の温度、縦軸にCO濃度を選んで示したグ
ラフ、第5図は本発明の他の実施態様を説明する
フローである。
Figure 1 is a flowchart explaining one embodiment of the present invention, and Figure 2 is a flowchart for explaining an embodiment of the present invention.
Graph showing the performance of various adsorbents during CO recovery, with adsorption pressure on the horizontal axis and CO concentration on the vertical axis, Part 3
The figure shows the CO recovery performance of various adsorbents at an adsorption temperature of 0°C, with the horizontal axis representing the desorption pressure and the vertical axis representing the CO concentration. Figure 4 shows the adsorption pressure at 1.2ata and the desorption pressure.
A graph showing the CO recovery performance of various adsorbents at 0.1 ata, with the temperature during adsorption on the horizontal axis and the CO concentration on the vertical axis. Figure 5 is a flowchart explaining another embodiment of the present invention. .

Claims (1)

【特許請求の範囲】 1 Na−A型ゼオライトにバインダを混合して
成形後熱処理してなるA型ゼオライト、Na−A
型ゼオライト(Naの18モル%までK置換したも
のを含む)にFeイオンを含浸させ、バインダを
混合して成形後、熱処理してなるA型ゼオライ
ト、及びNa−A型ゼオライトにFeイオンを含浸
させ、Naの18モル%までK置換し、バインダを
混合して成形後、熱処理してなるA型ゼオライト
よりなる群から選ばれたA型ゼオライトを、CO
吸収剤として充填した少なくとも2塔以上の吸着
塔に、CO,N2などを主として含有する混合ガス
を導き、吸着圧力1〜5ata、吸着温度室温〜−30
℃の操作条件でCO吸着を行わせた後、脱着圧力
0.05〜0.5ataの操作条件でCOを脱着させることを
特徴とするCO吸着分離方法。 2 吸着終了時の吸着塔に、回収されたCOガス
により吸着時と同一方向のガス流れで掃気した
後、脱着操作を行うことを特徴とする特許請求の
範囲第1記載の方法。
[Claims] 1. A-type zeolite, Na-A, which is obtained by mixing Na-A type zeolite with a binder and heat-treating the mixture after molding.
Type A zeolite (including those in which up to 18 mol% of Na is substituted with K) is impregnated with Fe ions, mixed with a binder, molded, and heat treated to produce Type A zeolite, and Na-A type zeolite impregnated with Fe ions. A-type zeolite selected from the group consisting of A-type zeolite obtained by substituting K up to 18 mol% of Na, mixing with a binder, molding, and heat-treating the A-type zeolite is
A mixed gas mainly containing CO, N2 , etc. is introduced into at least two or more adsorption towers packed as absorbents, at an adsorption pressure of 1 to 5 ata and an adsorption temperature of room temperature to -30 mA.
After CO adsorption at operating conditions of °C, the desorption pressure
A CO adsorption separation method characterized by desorbing CO under operating conditions of 0.05 to 0.5 ata. 2. The method according to claim 1, wherein the adsorption column is scavenged with the recovered CO gas at the end of adsorption with a gas flow in the same direction as during adsorption, and then the desorption operation is performed.
JP59038690A 1984-03-02 1984-03-02 Method of adsorption and separation of co Granted JPS60186410A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59038690A JPS60186410A (en) 1984-03-02 1984-03-02 Method of adsorption and separation of co

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59038690A JPS60186410A (en) 1984-03-02 1984-03-02 Method of adsorption and separation of co

Publications (2)

Publication Number Publication Date
JPS60186410A JPS60186410A (en) 1985-09-21
JPH0372007B2 true JPH0372007B2 (en) 1991-11-15

Family

ID=12532291

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59038690A Granted JPS60186410A (en) 1984-03-02 1984-03-02 Method of adsorption and separation of co

Country Status (1)

Country Link
JP (1) JPS60186410A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5108184B2 (en) * 2001-07-11 2012-12-26 大陽日酸株式会社 Carbon monoxide purification method

Also Published As

Publication number Publication date
JPS60186410A (en) 1985-09-21

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