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JPS6258772B2 - - Google Patents
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JPS6258772B2 - - Google Patents

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Publication number
JPS6258772B2
JPS6258772B2 JP58196122A JP19612283A JPS6258772B2 JP S6258772 B2 JPS6258772 B2 JP S6258772B2 JP 58196122 A JP58196122 A JP 58196122A JP 19612283 A JP19612283 A JP 19612283A JP S6258772 B2 JPS6258772 B2 JP S6258772B2
Authority
JP
Japan
Prior art keywords
carbon monoxide
absorbent
absorption
organic solvent
inorganic oxide
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
JP58196122A
Other languages
Japanese (ja)
Other versions
JPS6090037A (en
Inventor
Hidehiko Kudo
Sachio Asaoka
Shinichi Nakada
Tadami Kondo
Isao Suzuki
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.)
Chiyoda Corp
Original Assignee
Chiyoda Chemical Engineering and Construction Co 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 Chiyoda Chemical Engineering and Construction Co Ltd filed Critical Chiyoda Chemical Engineering and Construction Co Ltd
Priority to JP58196122A priority Critical patent/JPS6090037A/en
Publication of JPS6090037A publication Critical patent/JPS6090037A/en
Publication of JPS6258772B2 publication Critical patent/JPS6258772B2/ja
Granted legal-status Critical Current

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  • 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]

本発明は一酸化炭素(以下CO)吸収分離剤の
製造方法に関し、特にCOを選択的に吸収し、か
つ水に対する劣化性が少ない固体状の上記分離剤
の製造方法に関する。 従来、ガス分離用剤として式M〓M〓Xo・芳
香族(M〓:Cu等の第1−B族の金属、M〓:
Al等の第−A族の金属、X:ハロゲン、芳香
族:C6〜12の単環式芳香族炭化水素又はハロゲン
化芳香族炭化水素)の二金属塩錯体の芳香族炭化
水素又はハロゲン化芳香族炭化水素溶液からなる
液体状の吸収剤(特開昭57−21328号公報)、
CuAlX4(X:ハロゲン原子)を有する二金属塩
(特公昭48−35041号)等が提案されているが、こ
れらはいずれもプロピレン等の不飽和炭化水素ガ
スを吸収分離するためのものであり、またガス吸
収有効成分自体が不安定であつて、特に被処理ガ
ス中に水分が存在すると短期間に吸収性能を劣化
してしまうという欠点があつた。 最近になつて、ハロゲン化銅()、ハロゲ
ン化アルミニウム()、芳香族炭化水素よりな
る液体状の吸収剤(特開昭58−24321号公報)、
ハロゲン化銅()、ハロゲン化アルミニウム
()、ポリスチレン類よりなる固体状の吸収剤
(特開昭58−49436号公報)、ハロゲン化銅
()、ハロゲン化アルミニウム()、活性炭又
はグラフアイトよりなる固体状の吸収剤(特開昭
58−124516号公報)を用いて、製鉄所、製油所、
石油化学工場等で副生するCO含有混合ガス中か
ら、合成化学の基礎原料として有用なCOを選択
的に吸収分離する方法が提案された。 しかし、上記の液体状吸収剤は、前述の不飽
和炭化水素吸収剤と同様、水分に対する劣化性が
著るしく、長期間安定してCOを吸収分離するこ
とはできない。上記の固体吸収剤も耐水劣化性
が低く、しかもハロゲン化銅()とハロゲン化
アルミニウム()を担持し得る量が少ないとい
う問題があり、また上記の活性炭等で固体吸収
剤としたものは、水に対する劣化性は少ないもの
の、活性炭はCOに限らず、混合ガス中の他の成
分をも多量に吸着してしまい、COの選択性に欠
けるという難点を有している。 本発明は、これらの欠点を排除し、COの高選
択性吸収分離性能を有すると共に水に対する劣化
性が極めて少ない固体状のCO吸収分離剤を製造
し得る方法を提案するものである。 すなわち本発明は、ハロゲン化銅()および
ハロゲン化アルミニウム()の有機溶媒溶液
を、多孔性無機酸化物(アルミナを除く、以下同
じ)に十分接触させ、次いで遊離有機溶媒を除去
することを特徴とする一酸化炭素吸収分離剤の製
造法に関するものである。 本発明方法におけるハロゲン化銅()のハロ
ゲンとしては、塩素、臭素、ヨウ素、フツ素のい
ずれも有効であるが、コストや入手のし易さ等か
ら通常は塩化第1銅が使用される。 ハロゲン化アルミニウム()のハロゲンとし
ても、塩素、臭素、ヨウ素、フツ素のいずれも有
効であるが、通常は上記と同様の理由で塩化アル
ミニウムが使用される。なお、ハロゲン化アルミ
ニウム()は一般に不純物を含むので、昇華法
等によつて精製して用いられるが、前記した従来
の溶液法のように高度に精製する必要はない。 また、本発明方法における有機溶媒としては、
ベンゼン、トルエン、キシレン等の芳香族化合
物、二硫化炭素、ジクロルメタン等汎用のものが
使用される。 ただし、上記ハロゲン化銅()およびハロゲ
ン化アルミニウム()を溶解する能力がない溶
媒、あるいはこれら化合物を分解、還元、あるい
は酸化する溶媒は好ましくない。例えば、四塩化
炭素やクロロホルムは上記芳香族化合物に比しハ
ロゲン化アルミニウム()の溶解性が著しく低
く、本発明方法に使用することは不適である。ま
た、一般的に溶媒中に水が含まれる場合はハロゲ
ン化アルミニウム()が部分的に分解され固形
分とハロゲン酸を発生するので、使用溶媒中への
水分の混入は厳に避けるべきである。 更に、本発明方法で得られる吸収分離剤は、
CO吸収後の脱離操作が通常加温ないし減圧にて
行われるため、低沸点溶媒ないし高揮発性溶媒は
好ましくない。何故なら、本発明方法による吸収
分離剤は、後述するような錯塩と担体の無機酸化
物とが一体化したものであるが、その錯塩のハロ
ゲン化アルミニウム側が担体の無機酸化物と有機
溶媒との協同作用により疎水性に保たれていると
推定され、この有機溶媒が上記脱離操作の際に揮
発してしまうと、疎水性が失われ、水に対する劣
化性が大きくなるからである。 従つて、本発明方法においては、ベンゼン、ト
ルエン、キシレン等の芳香族化合物が好ましい有
機溶媒として挙げられる。 本発明方法において、上記のハロゲン化銅
()とハロゲン化アルミニウム()は、有機
溶媒に別々に、あるいは共に溶解させ、これを多
孔性無機酸化物に十分接触させる。接触方法は、
含浸法、浸漬法、噴霧法等が採用され、なかでも
必要以上に有機溶媒を使用せず、担体細孔容積に
ほぼ見合う量の溶液量で十分な含浸法が一般的で
ある。 ところで、本発明方法による吸収分離剤として
の能力は、銅が1価の状態で作用しているとき
に、著しいCO選択性、吸収性を示す。この銅を
1価で保持する働きを持つのがハロゲン化アルミ
ニウム()であり、特に以下に述べる錯塩中に
両者が等モルで〔例えばCuAlX4(X:ハロゲ
ン、以下同じ)等として〕存在しているときに能
力が最大となると考えられる。 そこで本発明方法においては、このような錯塩
を形成するために、上述の有機溶媒溶液を多孔性
無機酸化物に十分接触させた後に、水分がない状
態で、好ましくは不活性ガス中で、40〜60℃、4
〜2時間の加温操作を行う。この加温操作によ
り、Cu()、Al()、有機化合物、Xからな
る錯塩が形成され、また該錯塩は上述したように
担体の無機酸化物とも何らかの結合を形成するも
のと推定される。そして、この加温操作により、
遊離の有機溶媒も一部除去される。 なお、上記の加温操作は、有機溶媒溶液を多孔
性無機酸化物に接触される前であつてもよい。 ハロゲン化銅()とハロゲン化アルミニウム
()の比は、上述したようにモル比で1:1が
好ましく、余剰のハロゲン化アルミニウム()
が存在しないようにすることが望ましい。 有機溶媒溶液の濃度は、ハロゲン化銅()と
ハロゲン化アルミニウム()が溶解し得る濃度
であればよく、必要以上に希釈する必要はない。
一般的には、ハロゲン化銅()、ハロゲン化ア
ルミニウム()が、無機酸化物に対してトータ
ルで5〜50wt%担持される溶液濃度および量で
あればよい。 また、多孔性無機酸化物は、ハロゲン化銅
()とハロゲン化アルミニウム()が十分に
分散し得、かつ有機溶媒の一部とともに固定化し
得る能力を持つものが使用される。ただしCu
()を還元、酸化せず、しかもハロゲン化アル
ミニウム()を分解しないものである必要があ
る。 斯る多孔性無機酸化物としては、遊離水を含ま
ないもので、かつ十分な表面積を持つものが好ま
しい。表面積は余り大き過ぎると、必要以上に銅
ないしアルミニウムを固定不活性化したり、細孔
が小さくなり過ぎて錯塩の分散性を低下させる。
従つて、110〜1200℃、好ましくは450〜1100℃、
より好ましくは500〜900℃で焼成され、BET表
面積で40〜400m2/g、より好ましくは50〜350
m2/gとなつているものが好適であり、更に銅
()および/又はアルミニウム()をイオン
交換的に分散するような無機酸化物が選定され
る。具体的には、シリカ、シリカアルミナ、チタ
ニア、シリカマグネシア、ジルコニア、アルミナ
マグネシア等が使用され、特に優れた分散担持能
を示すシリカが好適である。 本発明方法においては前述の接触、加温操作の
後、遊離有機溶媒を減圧除去する。このとき前述
と同様の加温(すなわち、水分のない状態、好ま
しくは不活性ガス中で40〜60℃の加温)を加える
こともできる。この除去操作は液相状態の有機溶
媒がなくなるまで行うことが重要である。何故な
ら、本発明方法による固体状吸収分離剤が十分な
耐水性を発揮するのはCu()とAl()が多
孔性無機酸化物に完全に固定化している場合であ
り、遊離有機溶媒が液相状態で細孔内に保持され
たままであると、前述の従来の液体状吸収剤にみ
られるように水によつて容易にCOの選択吸収性
能を劣化してしまうからである。 次下、実施例をあげて本発明方法を更に具体的
に説明する。 実施例 1 塩化アルミニウム()は、市販の特級試薬
(ここではキシダ化学工業(株)製のもの)を昇華法
により精製し不純物を取り除いて用い、トルエン
は市販の特級試薬(ここでは和光純薬工業(株)製の
もの)を金属ナトリウムで脱水後、蒸留して使用
した。塩化銅()は市販の特級試薬(ここでは
小島化学薬品(株)製のもの)をそのまま使用した。 乾燥窒素下で、200mlのロータリーエバポレー
ター中に上記の塩化アルミニウム()0.8g
(6mmol)と上記の塩化銅()0.6g(6m
mol)を入れ、トルエン20mlを加えて溶解し、ロ
ータリーエバポレーターを回転し、かきまぜつ
つ、60℃で2時間加熱保温した。なお、上記の窒
素は市販の窒素(ここでは帝国酸素(株)製の純度
99.999%のもの)を使用直前に市販のモレキユラ
ーシーブ3A(ここでは日化精工(株)製のもの)を
充填した塔に通過させて精製したものを使用し
た。 一方、別の200mlロータリーエバポレーター
に、800℃にて焼成されて市販されているシリカ
ゲル(富士ダヴイソン社製商品名ID GEL、BET
表面積248m2/g)を10g入れ、真空ポンプを用
いてナスフラスコ内部を十分に脱気した後、この
中に滴下ロートを用いて、先に調製した塩化アル
ミニウム()および塩化銅()のトルエン溶
液を加えた。10分間かくはんを続けたのち、ロー
タリーエバポレーター内を減圧(6mmHg)にし
て一昼夜放置し、トルエンを十分に除去して吸収
剤を調整した。これにより得られた吸収剤は
11.93gであつた。 この吸収剤の性能を確認するため、200mlのロ
ータリーエバポレーター内に該吸収剤を入れ
1atmの一酸化炭素と窒素の混合ガス(一酸化炭
素分圧0.79atm、窒素分圧0.21atm)1を入れ
た容器と結合し、ロータリーエバポレーターを回
転しかきまぜつつ、26℃で一酸化炭素の吸収操作
を行つた。この吸収操作は一酸化炭素と窒素の混
合ガスをエアーポンプを用いて、1.4/minで
循環して吸収剤の上を通過させることにより行つ
た。なお、該一酸化炭素と窒素の混合ガスは市販
品(ここでは製鉄化学工業(株)製の純度CO:78.82
%、N2:21.18%のもの)を使用直前に市販の脱
酸素塔(日化精工(株)製のもの)を通過させて精製
したものを使用した。 一酸化炭素吸収量は、ガスビユーレツト法によ
り26℃で測定した。一酸化炭素の吸収は迅速で、
10分後の一酸化炭素吸収量は3.0mmolであつた。 次に、吸収剤を1atmで90℃に加熱し、吸収し
た一酸化炭素を放出させた。 一方、窒素ガス(上述の市販品を精製したも
の)1を入れた容器と、蒸留水を入れた洗気び
んを結合し、エアーポンプにて窒素ガスを洗気び
んに通すことにより26℃の飽和水蒸気圧分の水
(20000ppm)を窒素ガス中に混入し、該ガスを
上記の一酸化炭素放出後の吸収剤の上に0.8/
minで10分間循環させた(以下、この操作を水処
理という)。 その後、この吸収剤を26℃で、エバポレーター
を回転させながら1atmの一酸化炭素と窒素の混
合ガス(一酸化炭素分圧0.79atm、窒素分圧
0.21atm)(上述の市販品を精製したもの)1
を入れた容器と結合し、エアーポンプを用いて吸
収剤の上を循環させて再度一酸化炭素の吸収操作
を行つた。 この場合の一酸化炭素の吸収も迅速であり、10
分後には、2.1mmolの一酸化炭素を吸収した。 次に吸収剤を、1atmで90℃に加熱し、吸収し
た一酸化炭素を放出させた。 その後、上述の水処理、吸収、放出を繰返し、
一酸化炭素の吸収量を測定した。この結果を後述
の表−3に示す。 実施例 2〜6 実施例1の800℃にて焼成したシリカゲルの代
わりに表−1の無機酸化物を使用した以外は実施
例1と同様の操作を行つた。一酸化炭素の吸収量
を後述の表−3に合わせて示す。
The present invention relates to a method for producing a carbon monoxide (hereinafter CO) absorbing and separating agent, and particularly to a method for producing the above-mentioned solid separating agent that selectively absorbs CO and is less susceptible to water deterioration. Conventionally, as a gas separation agent, the formula M〓M〓
Aromatic hydrocarbon or halogenated dimetal salt complex of Group A metal such as Al, X: halogen, aromatic: C 6-12 monocyclic aromatic hydrocarbon or halogenated aromatic hydrocarbon Liquid absorbent consisting of aromatic hydrocarbon solution (Japanese Unexamined Patent Publication No. 57-21328),
Dimetallic salts containing CuAlX 4 (X: halogen atom) (Japanese Patent Publication No. 48-35041) have been proposed, but these are all for absorbing and separating unsaturated hydrocarbon gases such as propylene. Moreover, the effective gas absorption component itself is unstable, and the absorption performance deteriorates in a short period of time, especially when moisture is present in the gas to be treated. Recently, a liquid absorbent consisting of copper halide (2018), aluminum halide (2019), and aromatic hydrocarbons (Japanese Patent Application Laid-Open No. 58-24321),
A solid absorbent made of copper halide (), aluminum halide (), polystyrene (Japanese Unexamined Patent Publication No. 58-49436), copper halide (), aluminum halide (), activated carbon or graphite Solid absorbent (JP-A-Sho
58-124516), steel mills, oil refineries,
A method has been proposed to selectively absorb and separate CO, which is useful as a basic raw material for synthetic chemistry, from CO-containing mixed gases produced by petrochemical plants. However, the liquid absorbent described above, like the unsaturated hydrocarbon absorbent described above, has a remarkable deterioration property due to moisture, and cannot stably absorb and separate CO over a long period of time. The above-mentioned solid absorbent also has the problem of low water deterioration resistance and the amount of copper halide () and aluminum halide () that can be supported is small. Although activated carbon is less susceptible to water deterioration, it has the disadvantage that it adsorbs large amounts of not only CO but also other components in the mixed gas, and lacks selectivity for CO. The present invention eliminates these drawbacks and proposes a method for producing a solid CO absorption/separation agent that has highly selective absorption and separation performance for CO and has extremely low deterioration with respect to water. That is, the present invention is characterized in that an organic solvent solution of copper halide () and aluminum halide () is brought into sufficient contact with a porous inorganic oxide (excluding alumina, the same shall apply hereinafter), and then free organic solvent is removed. The present invention relates to a method for producing a carbon monoxide absorption and separation agent. As the halogen for the copper halide (2) in the method of the present invention, any of chlorine, bromine, iodine, and fluorine are effective, but cuprous chloride is usually used because of its cost and availability. Any of chlorine, bromine, iodine, and fluorine are effective as the halogen of aluminum halide (), but aluminum chloride is usually used for the same reason as above. Note that since aluminum halide (2) generally contains impurities, it is purified by a sublimation method or the like before use, but it does not need to be purified to a high degree as in the conventional solution method described above. In addition, as the organic solvent in the method of the present invention,
Aromatic compounds such as benzene, toluene, and xylene, and general-purpose compounds such as carbon disulfide and dichloromethane are used. However, solvents that do not have the ability to dissolve the copper halide () and aluminum halide (), or solvents that decompose, reduce, or oxidize these compounds are not preferred. For example, carbon tetrachloride and chloroform have significantly lower solubility of aluminum halide () than the above-mentioned aromatic compounds, and are therefore unsuitable for use in the method of the present invention. Additionally, if the solvent contains water, the aluminum halide () will be partially decomposed and generate solids and halogen acids, so contamination of water into the solvent used should be strictly avoided. . Furthermore, the absorption separation agent obtained by the method of the present invention is
Since the desorption operation after CO absorption is usually performed under heating or reduced pressure, low boiling point solvents or highly volatile solvents are not preferred. This is because the absorption/separation agent according to the method of the present invention is a product in which a complex salt and an inorganic oxide as a carrier are integrated as described below, but the aluminum halide side of the complex salt is a mixture of the inorganic oxide of the carrier and the organic solvent. This is because it is presumed that hydrophobicity is maintained by a cooperative action, and if this organic solvent evaporates during the above-mentioned desorption operation, hydrophobicity is lost and the deterioration property with respect to water increases. Therefore, in the method of the present invention, aromatic compounds such as benzene, toluene, and xylene are preferred as organic solvents. In the method of the present invention, the above-mentioned copper halide (2) and aluminum halide (2) are dissolved separately or together in an organic solvent and brought into sufficient contact with the porous inorganic oxide. The contact method is
Impregnation methods, dipping methods, spraying methods, etc. are employed, and among them, the impregnation method is generally used, in which an amount of solution approximately corresponding to the pore volume of the carrier is sufficient without using an excessive amount of organic solvent. By the way, the ability of the method of the present invention as an absorption/separation agent shows remarkable CO selectivity and absorption when copper is acting in a monovalent state. Aluminum halide () has the function of retaining this copper in a monovalent state, and especially in the complex salts described below, both are present in equimolar amounts [for example, as CuAlX 4 (X: halogen, the same hereinafter)]. It is thought that the ability is at its maximum when the Therefore, in the method of the present invention, in order to form such a complex salt, after bringing the above-mentioned organic solvent solution into sufficient contact with the porous inorganic oxide, it is heated for 40 minutes in the absence of water, preferably in an inert gas. ~60℃, 4
Perform a warming operation for ~2 hours. Through this heating operation, a complex salt consisting of Cu(), Al(), the organic compound, and X is formed, and the complex salt is also presumed to form some kind of bond with the inorganic oxide of the carrier as described above. And, with this heating operation,
Some free organic solvent is also removed. Note that the above heating operation may be performed before the organic solvent solution is brought into contact with the porous inorganic oxide. As mentioned above, the ratio of copper halide () to aluminum halide () is preferably 1:1 in terms of molar ratio, and the excess aluminum halide ()
It is desirable to ensure that there is no such thing. The concentration of the organic solvent solution may be such that copper halide (2) and aluminum halide (2) can be dissolved, and there is no need to dilute it more than necessary.
Generally, the solution concentration and amount may be such that copper halide (2) and aluminum halide (2) are supported in a total amount of 5 to 50 wt% relative to the inorganic oxide. Furthermore, the porous inorganic oxide used has the ability to sufficiently disperse copper halide (2) and aluminum halide (2) and to immobilize it together with a portion of the organic solvent. However, Cu
It needs to be something that does not reduce or oxidize () and also does not decompose aluminum halide (). Such porous inorganic oxides preferably do not contain free water and have a sufficient surface area. If the surface area is too large, copper or aluminum may be fixed and inactivated more than necessary, or the pores may become too small, reducing the dispersibility of the complex salt.
Therefore, 110-1200℃, preferably 450-1100℃,
More preferably calcined at 500-900°C, with BET surface area of 40-400 m 2 /g, more preferably 50-350
m 2 /g is preferable, and an inorganic oxide that disperses copper (2) and/or aluminum (2) in an ion-exchange manner is selected. Specifically, silica, silica alumina, titania, silica magnesia, zirconia, alumina magnesia, etc. are used, and silica, which exhibits particularly excellent dispersion and supporting ability, is preferred. In the method of the present invention, after the above-mentioned contacting and heating operations, the free organic solvent is removed under reduced pressure. At this time, the same heating as described above (that is, heating at 40 to 60° C. in a moisture-free state, preferably in an inert gas) can also be applied. It is important to carry out this removal operation until the organic solvent in the liquid phase is exhausted. This is because the solid absorption and separation agent produced by the method of the present invention exhibits sufficient water resistance only when Cu() and Al() are completely immobilized in the porous inorganic oxide, and free organic solvent is This is because if it remains in the pores in a liquid state, the selective absorption performance of CO will easily deteriorate due to water, as seen in the conventional liquid absorbent mentioned above. The method of the present invention will now be explained in more detail with reference to Examples. Example 1 Aluminum chloride () was used by purifying a commercially available special grade reagent (here, produced by Kishida Chemical Industry Co., Ltd.) by a sublimation method to remove impurities, and toluene was used as a commercially available special grade reagent (here, produced by Wako Pure Chemical Industries, Ltd.). (manufactured by Kogyo Co., Ltd.) was dehydrated with metallic sodium, distilled, and used. As copper chloride (), a commercially available special grade reagent (here, manufactured by Kojima Chemical Co., Ltd.) was used as is. 0.8 g of the above aluminum chloride () in a 200 ml rotary evaporator under dry nitrogen
(6 mmol) and the above copper chloride () 0.6 g (6 m
mol), added 20 ml of toluene to dissolve, and heated and kept at 60°C for 2 hours while stirring on a rotary evaporator. Note that the above nitrogen is commercially available nitrogen (here, high-purity nitrogen manufactured by Teikoku Sanso Co., Ltd.).
99.999%) was purified immediately before use by passing it through a column filled with commercially available Molecular Sieve 3A (here manufactured by Nikka Seiko Co., Ltd.). On the other hand, in another 200 ml rotary evaporator, commercially available silica gel (manufactured by Fuji Davison, product name ID GEL, BET) was calcined at 800°C.
After thoroughly degassing the inside of the eggplant flask using a vacuum pump, add toluene containing the previously prepared aluminum chloride () and copper chloride ( ) using a dropping funnel. solution was added. After stirring for 10 minutes, the pressure inside the rotary evaporator was reduced (6 mmHg) and the mixture was left overnight to sufficiently remove toluene and prepare an absorbent. The absorbent obtained by this is
It weighed 11.93g. To check the performance of this absorbent, it was placed in a 200ml rotary evaporator.
Combined with a container containing 1 atm carbon monoxide and nitrogen mixed gas (carbon monoxide partial pressure 0.79 atm, nitrogen partial pressure 0.21 atm) 1, absorption of carbon monoxide at 26°C while rotating a rotary evaporator. I performed the operation. This absorption operation was carried out by circulating a mixed gas of carbon monoxide and nitrogen at 1.4/min using an air pump and passing it over the absorbent. The mixed gas of carbon monoxide and nitrogen is a commercially available product (purity CO: 78.82 manufactured by Steel Chemical Industry Co., Ltd.).
%, N2 : 21.18%) was purified by passing it through a commercially available deoxidation tower (manufactured by Nikka Seiko Co., Ltd.) immediately before use. The amount of carbon monoxide absorbed was measured at 26°C by the gas biuret method. Carbon monoxide absorption is rapid;
The amount of carbon monoxide absorbed after 10 minutes was 3.0 mmol. The absorbent was then heated to 90° C. at 1 atm to release the absorbed carbon monoxide. On the other hand, a container containing nitrogen gas (purified from the above-mentioned commercial product) 1 is combined with an air washing bottle containing distilled water, and an air pump is used to pass nitrogen gas through the air washing bottle to maintain a temperature of 26°C. Water (20,000 ppm) corresponding to the saturated water vapor pressure is mixed into nitrogen gas, and the gas is poured onto the absorbent after carbon monoxide is released at 0.8%.
min for 10 minutes (hereinafter, this operation is referred to as water treatment). After that, this absorbent was heated to 26°C with a mixed gas of 1 atm carbon monoxide and nitrogen (carbon monoxide partial pressure 0.79 atm, nitrogen partial pressure
0.21atm) (purified from the above commercial product) 1
The absorbent was connected to a container containing carbon monoxide, and an air pump was used to circulate the absorbent over the absorbent to perform the carbon monoxide absorption operation again. The absorption of carbon monoxide in this case is also rapid, with 10
After minutes, 2.1 mmol of carbon monoxide was absorbed. The absorbent was then heated to 90° C. at 1 atm to release the absorbed carbon monoxide. After that, the above water treatment, absorption and release are repeated,
The amount of carbon monoxide absorbed was measured. The results are shown in Table 3 below. Examples 2 to 6 The same operations as in Example 1 were performed except that the inorganic oxides shown in Table 1 were used instead of the silica gel calcined at 800°C in Example 1. The amount of carbon monoxide absorbed is also shown in Table 3 below.

【表】 実施例 7〜8 実施例1のトルエンの代りに表−2の溶媒を使
用した以外は、実施例1と同様の操作を行つた。
結果を表−3に合わせて示す。
[Table] Examples 7 to 8 The same operations as in Example 1 were performed except that the solvents shown in Table 2 were used instead of toluene in Example 1.
The results are also shown in Table-3.

【表】【table】

〔選択吸収能についての比較試験〕[Comparative test on selective absorption capacity]

実施例1で製造した吸収剤と、活性炭(武田薬
品製白鷺C表面積約1300m2/g)をシリカゲルの
代りに用いて実施例1の製造条件に準拠して製造
した吸収剤について、一酸化炭素の選択吸収能を
比較するために、一酸化炭素、二酸化炭及び窒素
からなる混合ガス(CO分圧0.71atm、CO2分圧
0.10atm、N2分圧0.19atm)を用いた比較試験を
行なつた。 それぞれの吸収剤を10gづつ採取して実施例1
の試験条件の下でガス吸収量を測定したところ、
実施例1の吸収剤は一酸化炭素を1.7mmol、二酸
化炭素を0.03mmol吸収したが上記活性炭を用い
た吸収剤は一酸化炭素を2.2mmol、二酸化炭素を
0.24mmol吸収した。なお、上記の活性炭より表
面積の小さな活性炭を用いて上記と同様の性能試
験を行なつたが、ガス吸収量は上記とほぼ同じで
あつた。 以上の試験より実施例1の吸収剤におけるシリ
カゲルの代りに活性炭を用いた吸収剤は一酸化炭
素を吸収するとともに相当量の二酸化炭素を吸収
するのに対して、実施例1の吸収剤は二酸化炭素
の吸収量が低く、一酸化炭素の選択吸収能が非常
に優れていることがわかる。 以上の実施例、比較例及び比較試験から明らか
なように、本発明方法で製造される一酸化炭素吸
収分離剤は、一酸化炭素の選択吸収能に優れ、水
に対する劣化の度合が極めて低く、長期間安定し
て一酸化炭素の吸収分離に供することができるも
のである。
Regarding the absorbent manufactured in Example 1 and the absorbent manufactured according to the manufacturing conditions of Example 1 using activated carbon (Shirasagi C surface area of Takeda Pharmaceutical Co., Ltd., approximately 1300 m 2 /g) in place of silica gel, carbon monoxide A mixed gas consisting of carbon monoxide, carbon dioxide and nitrogen (CO partial pressure 0.71 atm, CO 2 partial pressure
A comparative test was conducted using N2 partial pressure of 0.10atm and N2 partial pressure of 0.19atm. Example 1: 10g of each absorbent was collected.
When the gas absorption amount was measured under the test conditions of
The absorbent of Example 1 absorbed 1.7 mmol of carbon monoxide and 0.03 mmol of carbon dioxide, but the absorbent using activated carbon absorbed 2.2 mmol of carbon monoxide and 0.03 mmol of carbon dioxide.
Absorbed 0.24 mmol. A performance test similar to the above was conducted using activated carbon having a smaller surface area than the above activated carbon, but the gas absorption amount was almost the same as above. From the above tests, the absorbent of Example 1 that uses activated carbon instead of silica gel absorbs not only carbon monoxide but also a considerable amount of carbon dioxide, whereas the absorbent of Example 1 uses activated carbon instead of silica gel. It can be seen that the amount of carbon absorbed is low and the selective absorption ability of carbon monoxide is very excellent. As is clear from the above Examples, Comparative Examples, and Comparative Tests, the carbon monoxide absorption and separation agent produced by the method of the present invention has excellent selective absorption ability for carbon monoxide, and has an extremely low degree of deterioration with respect to water. It can be stably used for absorption and separation of carbon monoxide for a long period of time.

Claims (1)

【特許請求の範囲】 1 ハロゲン化銅()およびハロゲン化アルミ
ニウム()の有機溶媒溶液を、多孔性無機酸化
物(アルミナを除く)に十分接触させ、次いで遊
離有機溶媒を除去することを特徴とする一酸化炭
素吸収分離剤の製造法。 2 500〜900℃で焼成され、表面積が50〜350
m2/gの多孔性無機酸化物(アルミナを除く)を
使用することを特徴とする特許請求の範囲1記載
の方法。 3 多孔性無機酸化物としてシリカを使用するこ
とを特徴とする特許請求の範囲1又は2記載の方
法。 4 有機溶媒として芳香族化合物を使用すること
を特徴とする特許請求の範囲1、2又は3記載の
方法。
[Claims] 1. A method characterized in that an organic solvent solution of copper halide () and aluminum halide () is brought into sufficient contact with a porous inorganic oxide (excluding alumina), and then free organic solvent is removed. A method for producing a carbon monoxide absorption and separation agent. 2 Fired at 500-900℃, surface area 50-350
2. A method as claimed in claim 1, characterized in that a porous inorganic oxide (excluding alumina) of m 2 /g is used. 3. The method according to claim 1 or 2, characterized in that silica is used as the porous inorganic oxide. 4. The method according to claim 1, 2 or 3, characterized in that an aromatic compound is used as the organic solvent.
JP58196122A 1983-10-21 1983-10-21 Preparation of carbon monoxide absorbing and separating agent Granted JPS6090037A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58196122A JPS6090037A (en) 1983-10-21 1983-10-21 Preparation of carbon monoxide absorbing and separating agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58196122A JPS6090037A (en) 1983-10-21 1983-10-21 Preparation of carbon monoxide absorbing and separating agent

Publications (2)

Publication Number Publication Date
JPS6090037A JPS6090037A (en) 1985-05-21
JPS6258772B2 true JPS6258772B2 (en) 1987-12-08

Family

ID=16352604

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58196122A Granted JPS6090037A (en) 1983-10-21 1983-10-21 Preparation of carbon monoxide absorbing and separating agent

Country Status (1)

Country Link
JP (1) JPS6090037A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0672005B2 (en) * 1985-11-08 1994-09-14 千代田化工建設株式会社 Method for adsorption and separation of carbon monoxide
JPS6372337A (en) * 1986-09-12 1988-04-02 Asada Kagaku Kogyo Kk Adsorbent
US8210024B2 (en) 2009-10-16 2012-07-03 The Boeing Company Damage impactor

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6049022B2 (en) * 1982-01-22 1985-10-30 英史 平井 How to separate carbon monoxide from mixed gas
JPS58156516A (en) * 1982-03-13 1983-09-17 Toho Rayon Co Ltd Fibrous activated carbon and method for using the same

Also Published As

Publication number Publication date
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