JPH048368B2 - - Google Patents
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- Publication number
- JPH048368B2 JPH048368B2 JP61098509A JP9850986A JPH048368B2 JP H048368 B2 JPH048368 B2 JP H048368B2 JP 61098509 A JP61098509 A JP 61098509A JP 9850986 A JP9850986 A JP 9850986A JP H048368 B2 JPH048368 B2 JP H048368B2
- Authority
- JP
- Japan
- Prior art keywords
- cosorb
- solution
- gas
- ppm
- less
- 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
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K3/00—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide
- C10K3/02—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide by catalytic treatment
- C10K3/04—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide by catalytic treatment reducing the carbon monoxide content, e.g. water-gas shift [WGS]
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/40—Carbon monoxide
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- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Inorganic Chemistry (AREA)
- Carbon And Carbon Compounds (AREA)
- Industrial Gases (AREA)
- Catalysts (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
Description
[産業上の利用分野]
本発明はCOを主成分とする含O2ガスよりO2を
効率的に除去し、更にCOSORB法によつてCOを
分離回収する方法に関するものである。
[従来の技術]
最近、CO、CO2、CH3OHなどの炭素数が1つ
の化合物を出発原料とするC1化学が注目を集め
ているが、上記C1化合物の中でも特にCOは、(1)
反応活性がきわめて強いこと、(2)これまで利用価
値が低いとされてきた重質油、タールサンド、石
炭などのガス化により容易に製造できることのほ
か、(3)製鉄所副生ガス、メタノールプラントバー
ジンガスなど各種工業からの副生ガスとして大量
に得られること等から、特に有望な原料と考えら
れている。
COの分離・精製技術としては、アンモニア性
銅液洗浄法や深冷分離法などが知られているが、
米国テネコ・ケミカル社とエツソ・リサーチ・ア
ンド・エンジニアリング社が協同開発した所謂
「COSORBプロセス」(特公昭48−3504号公報参
照)は、各種混合ガスから高純度のCOを高収率
かつ安価に回収するプロセスとして、今後C1化
学の発展に重要な役割を果たすものと期待されて
いる。
COSORBプロセスで使用される吸収液(以下
COSORB溶液という)とは、M〓M〓Xn・芳香族
(2種の金属からなる塩錯体の芳香族炭化水素の
溶液)として表わされるものであるが、中でも特
に好ましい溶液は、ハロゲン化第1銅とハロゲン
化アンモニウムとを適当な溶媒中で反応させるこ
とによつて製造させる一般式CuAlX4(X:ハロ
ゲン原子、例えばCl)を有する2金属の塩錯体の
芳香族炭化水素(例えばトルエン)溶液である。
但し本発明においてはCOSORB溶液の構成が特
定される訳ではなく、今後開発されるであろう
COSORB溶液は全て本発明の対象に含まれる。
各種文献によるとCOSORB溶液は、H2、CO2、
CH4、N2、O2などに対しては化学的に不活性で
あると取扱われており、実際にCOを主成分とす
る含O2ガスをCOSORBプロセスで処理する際に
はO2を除去せずにそのままCOSORB溶液と接触
させ、COを分離回収している。
[発明が解決しようとする問題点]
たとえば、製鉄所の転炉ガスからCOを回収す
る場合(転炉ガスは一般にCO:約70%、CO2:
約17%、N2:約10%、H2:約2%、O2:0.2〜
1.5%程度含む)、この混合ガスを昇圧して活性炭
吸着塔等に供給することにより微量不純物例えば
H2S、SO2、NH3、HCN等を除去し、更に合成
ゼオライト等の充填された吸着塔に供給すること
によつて水分を1ppm以下に除去した後COSORB
プロセスに供給してCOを分離回収する。
COSORBプロセスに供給された転炉ガスは吸
収塔でCOSORB溶液と向流接触し、常温下では
COが選択的に吸収される。COを吸収した
COSORB溶液は放散塔に送られ、ここで加温さ
れてCOを放散する一方COSORB溶液は回収され
循環使用される。得られたCOはC1化合物の原料
として、或はその他種々の目的に使用される。
CuAlCl4・C7H8+CO
常温
→
←
高温CuAlCl4・CO+C7H8
ところが、転炉ガスを原料として長期間
COSORBプロセスを運転していると、COSORB
溶液の劣化とCOSORBプロセスの熱交換器の閉
塞という問題が生じてきた。
これらの問題は後述するように混合ガス中に含
まれるO2によるものであることが本発明者らの
検討の結果判明した。
そこで本発明においては、COSORBプロセス
導入前の混合ガス中のO2を効果的に取り除き得
る技術の開発を主眼点とし、その結果として、
COSORB溶液の劣化およびCOSORBプロセスの
熱交換器閉塞を防ぎCOSORBプロセスの長期運
転を可能とするCOの精製方法の確立を目的とす
るものである。
[問題点を解決するための手段]
上記問題点を解決することのできた本発明とは
COを主成分とし、3容量%以下のO2を含有する
混合ガスを、少なくとも銅を含有する触媒の充填
された脱酸素装置に80℃以下で導入し、主として
O2をCO2に変換することによつてO2含有量を100
容量ppm以下に低下させてから、金属錯塩の芳香
族炭化水素溶液に供給してCOの精製を行うこと
を要旨とするものである。
[作用]
COSORB溶液は、塩化第1銅(CuCl)よりも
強いルイス塩基あるいは、含酸素有機化合物と反
応し、COSORB溶液が分解して、塩化第1銅、
塩化水素あるいは室温タール等を生成する。
前記した(a)COSORB溶液の劣化、(b)COSORB
プロセスの熱交換器閉塞といつた問題を追跡して
いたところ、COSORB溶液中に室温タールが指
数関数的に生成増加し、塩化水素の発生も指数関
数的に増加してくることが判明した。この原因を
研究するために本発明者らは次のような実験を行
なつた。
(実験1)
500c.c.のメスフラスコに300c.c.のCOSORB溶液
(液温130℃)を入れ、2%O2−98%N2の混合標
準ガス250c.c./minを吹込んだ場合と、純N2ガス
及び純COガスを同じく250c.c./minで、同温度の
液中に吹込んだ場合の結果を第3図及び第1表に
示す。
以上から明らかな様に、O2が含まれている場
合にはCOSORB溶液がO2と反応して
液中の銅溶解量が減少した。
室温タールの量が増えた。
塩化水素が発生し続けた。
これに対し、O2が除去されたガス、すなわち
純N2、純COをCOSORB溶液に吹込むと、上記
のようになCOSORB溶液の劣化現象は確認され
なかつた。
又、COを主成分とするO2含有ガスを長時間処
理したCOSORB溶液について、これをガスクロ
マトグラフで分析するとメチレンビスメチルベン
ゼン
[Industrial Application Field] The present invention relates to a method for efficiently removing O 2 from an O 2 -containing gas containing CO as a main component, and further separating and recovering CO by the COSORB method. [Prior Art] Recently, C1 chemistry that uses compounds with one carbon number as starting materials, such as CO, CO 2 and CH 3 OH, has been attracting attention, but among the above C1 compounds, especially CO ( 1)
It has extremely strong reaction activity, (2) can be easily produced by gasifying heavy oil, tar sand, coal, etc., which have been considered to have low utility value, and (3) steelworks byproduct gas, methanol. It is considered to be a particularly promising raw material because it can be obtained in large quantities as a by-product gas from various industries such as plant virgin gas. Known CO separation and purification technologies include the ammoniacal copper solution cleaning method and the cryogenic separation method.
The so-called "COSORB process" (see Japanese Patent Publication No. 1983-3504), jointly developed by Tenneco Chemical Company and Etsuo Research and Engineering Company in the United States, produces high-purity CO from various mixed gases in high yield and at low cost. As a recovery process, it is expected to play an important role in the future development of C1 chemistry. Absorbent liquid used in the COSORB process (hereinafter referred to as
(referred to as COSORB solution) is expressed as M〓M〓Xn・aromatic (a solution of an aromatic hydrocarbon of a salt complex consisting of two metals), and a particularly preferred solution is a halogenated primary An aromatic hydrocarbon (e.g. toluene) solution of a bimetallic salt complex having the general formula CuAlX 4 (X: halogen atom, e.g. Cl) produced by reacting copper and ammonium halide in a suitable solvent. It is.
However, the composition of the COSORB solution is not specified in the present invention, and will be developed in the future.
All COSORB solutions are included in the scope of the present invention. According to various literature, COSORB solution contains H 2 , CO 2 ,
CH 4 , N 2 , O 2 , etc. are treated as chemically inert, and in fact, when O 2 -containing gas containing CO as its main component is processed in the COSORB process, O 2 is removed. CO is separated and recovered by contacting it directly with the COSORB solution without removing it. [Problems to be solved by the invention] For example, when recovering CO from converter gas in a steel mill (converter gas generally contains about 70% CO and CO 2 :
Approx. 17%, N 2 : approx. 10%, H 2 : approx. 2%, O 2 : 0.2~
This mixed gas is pressurized and supplied to an activated carbon adsorption tower etc. to remove trace impurities such as
After removing H 2 S, SO 2 , NH 3 , HCN, etc., and further removing water to below 1 ppm by supplying it to an adsorption tower filled with synthetic zeolite, COSORB
It is supplied to the process and CO is separated and recovered. The converter gas supplied to the COSORB process is in countercurrent contact with the COSORB solution in the absorption tower, and at room temperature
CO is selectively absorbed. absorbed CO
The COSORB solution is sent to a stripping tower where it is heated and CO is stripped off, while the COSORB solution is recovered and recycled. The obtained CO is used as a raw material for C 1 compounds or for various other purposes. CuAlCl 4・C 7 H 8 +CO Room temperature → ← High temperature CuAlCl 4・CO+C 7 H 8However , it is difficult to use converter gas as a raw material for a long period of time.
When running the COSORB process, COSORB
Problems have arisen with solution deterioration and heat exchanger blockage in the COSORB process. As a result of studies by the present inventors, it has been found that these problems are caused by O 2 contained in the mixed gas, as will be described later. Therefore, the main focus of the present invention is to develop a technology that can effectively remove O 2 from the mixed gas before introducing the COSORB process, and as a result,
The purpose of this study is to establish a CO purification method that prevents COSORB solution deterioration and COSORB process heat exchanger blockage, and enables long-term operation of the COSORB process. [Means for solving the problems] What is the present invention that can solve the above problems?
A mixed gas containing CO as the main component and 3% by volume or less of O 2 is introduced at 80°C or below into a deoxidizer packed with a catalyst containing at least copper, and
100% O2 content by converting O2 to CO2
The gist of this method is to purify CO by reducing the volume to below ppm and then supplying it to an aromatic hydrocarbon solution of a metal complex salt. [Action] The COSORB solution reacts with a Lewis base stronger than cuprous chloride (CuCl) or an oxygen-containing organic compound, and the COSORB solution decomposes to form cuprous chloride, cuprous chloride,
Generates hydrogen chloride or room temperature tar. (a) Deterioration of COSORB solution, (b) COSORB
While tracking problems such as heat exchanger blockage in the process, it was discovered that the formation of room temperature tar in the COSORB solution was increasing exponentially, and the generation of hydrogen chloride was also increasing exponentially. In order to study the cause of this, the present inventors conducted the following experiment. (Experiment 1) Put 300c.c. of COSORB solution (liquid temperature 130℃) into a 500c.c. volumetric flask, and blow in 250c.c./min of mixed standard gas of 2% O 2 - 98% N 2 . Figure 3 and Table 1 show the results when pure N 2 gas and pure CO gas were blown into the liquid at the same temperature at 250 c.c./min. As is clear from the above, when O 2 was included, the COSORB solution reacted with O 2 and the amount of copper dissolved in the solution decreased. The amount of room temperature tar has increased. Hydrogen chloride continued to evolve. On the other hand, when gas from which O 2 was removed, ie, pure N 2 and pure CO, was blown into the COSORB solution, the above-mentioned deterioration phenomenon of the COSORB solution was not observed. Furthermore, when a COSORB solution treated with O2 - containing gas, which is mainly composed of CO, for a long period of time is analyzed by gas chromatography, methylenebismethylbenzene is detected.
【式】の存在が確
認された。
以上のことから、COSORB溶液中に溶解して
いる塩化水素(HCl)、トルエンと処理ガス中の
O2とが反応し、下記(1)、(2)、(3)、(4)[(4)式は(1)、
(2)、(3)式をまとめたもの]のような反応が
COSORB溶液中で起こり、COSORB溶液の劣
化、すなわち室温タールの生成、塩化水素の発
生、液中銅溶解量の減少等が生じ、COSORBプ
ロセスにとつて重大な問題が起こつたのではない
かと考えられた。
H2O+CuAlCl4 →CuCl↓+AlOCl+2HCl↑ ……(3)
*ただしPolymerは
が
徐々に重合成長したもの)
即ちCOを主成分とするO2含有ガスをCOSORB
プロセスで処理すると液劣化が起こり、高価な
COSORB溶液が失われるとともに、生成した室
温タールおよび生成したCuClあるいはAlOClが
スラツジとして熱交換器にスケーリングし、熱交
換器を閉塞し、長期間の運転が困難になつてくる
というわけである。The existence of [Formula] has been confirmed. From the above, it can be concluded that hydrogen chloride (HCl) dissolved in the COSORB solution, toluene and the processing gas
O 2 reacts, and the following (1), (2), (3), (4) [(4) formula is (1),
(2) and (3) are summarized]
This occurred in the COSORB solution, resulting in deterioration of the COSORB solution, including the formation of room temperature tar, generation of hydrogen chloride, and a decrease in the amount of copper dissolved in the solution, which was thought to have caused serious problems for the COSORB process. . H 2 O+CuAlCl 4 →CuCl↓+AlOCl+2HCl↑ ……(3) *However, Polymer COSORB is a gas containing O 2 whose main component is CO
Processing causes liquid deterioration, resulting in expensive
As the COSORB solution is lost, the generated room temperature tar and the generated CuCl or AlOCl scale as sludge in the heat exchanger, clogging the heat exchanger and making long-term operation difficult.
【表】
(実験2)
実験1と同様の条件で2%O2−98%N2の混合
標準ガス250c.c./minを液中に約60時間吹込んだ
後、純N2ガスに切替えると、第4図に示すよう
に数時間後に塩化水素発生速度は急減した。この
結果から含O2ガスでは、COSORB溶液の劣化現
象指標となる塩化水素の発生が続き、O2を含ん
でいないガスでは塩化水素が発生しないことが確
認された。
したがつて混合ガス中のO2を除去した後で
COSORBプロセスに供給する様にすれば、これ
らのトラブルをなくすことができるはずであると
の確信を得るに至つたが、種々検討した結果、3
容量%以下のO2を含有する原料ガスであれば、
本発明で特定した触媒を用いることによつて容易
に100容量ppm以下、条件によつては10〜1ppm以
下に低減させることが可能であり、所期の目的が
達成され得ることを知つた。又、原料ガスを
COSORBプロセスに供給する前に、あらかじめ
O2を100ppm以下に除去するため精製されたCO
中のO2濃度も低減し、精製COの純度が改善され
るという副次効果もあらわれる。更に本発明に用
いられる触媒は銅系あるいは銅および他の金属例
えば、亜鉛、マンガン、クロム、ニツケル等との
2元組成のものであり、特に反応活性及び反応選
択性に優れ、かつCOSORB溶液にとつて有害な
H2S等の不純ガス吸着除去できる意味で40〜60%
酸化銅/60〜40%酸化亜鉛が最適である。以下
O2の除去プロセスを中心にして更に説明する。
COを主成分とし3容量%以下のO2を含有する
混合ガスを、上記触媒の充填された脱酸素装置に
10〜80℃、好ましくは20〜50℃で導入すると、
O2は主としてCO2になりO2が除去される。
CO+1/2O2→CO2
本発明ではO2含有量の上限が3容量%である
と述べたが実際問題として転炉ガスや高炉ガス中
のO2量が3容量%を超えることはないので実用
上は無制限と考えても良い。触媒を用いる場合に
おいても、他の一般的な触媒反応と同様に反応選
択率の問題があり、
H2+1/2O2→H2O
3H2+CO→H2O+CH4
のような反応がすすむ可能性が1%でもあれば
H2OによりCOSORB液が劣化するので、後の工
程で脱湿する必要がある。本発明が特定した触媒
は、CO+1/2O2→CO2の低温活性及び反応選択性
が非常に大きいが、副反応であるH2+1/2O2→
H2O等の反応を極力抑制するためには、脱酸素
装置での入口ガス温度を低くする方が良く、80℃
以下、好ましくは50℃以下で含O2ガスを導入す
る方が良い。またCu系触媒はメタノール合成触
媒としても使用されているので
CO+2H2→CH3OH
2CO+4H2→CH3OCH3+H2O
2CO+2H2→CH3COOH
の反応がおこることもあり、メタノールやエーテ
ルのような含酸素有機化合物によるCOSORB溶
液の劣化が起こることが想定される。そのため脱
酸素装置出口温度を230℃以下にすることが好ま
しく、脱酸素装置に導入される含O2ガスを10〜
80℃、好ましくは20〜50℃で供給する。O2濃度
が高い時には脱酸素装置の中に冷却器等を設置し
たりして、出口温度が230℃以下になるようにし、
含酸素有機化合物の含有量を50容易ppm以下、好
ましくは10ppm以下にすることが望ましい。メタ
ノール等は、水と同様に合成ゼオライト等を充填
した吸着塔にて除去が可能であるが、吸着塔の再
生時に温度を上げるためメタノール等が分解し、
炭素析出が起こつたり、又合成ゼオライトと化学
反応し、脱着しなくなる可能性が考えられる。そ
のため、脱酸素装置出口での含酸素有機化合物濃
度は50容量ppm以下にすることが望ましい。こう
してO2含有量を100容量ppm、好ましくは10ppm
以下に低下させた混合ガスは必要に応じ脱湿及び
脱メタノール後COSORBプロセスに供給される。
ここでO2含有量を100容量ppm以下とした理由は
次の通りである。
すなわち、前記試験結果をもとにCOSORB溶
液へのO2含有ガスのO2濃度と液劣化速度との関
係から同O2濃度の液寿命を対応させて表わすと
第2表の通りである。[Table] (Experiment 2) Under the same conditions as Experiment 1, after blowing 250 c.c./min of standard mixed gas of 2% O 2 -98% N 2 into the liquid for about 60 hours, pure N 2 gas was added. When the switch was made, the hydrogen chloride generation rate suddenly decreased after several hours as shown in FIG. From this result, it was confirmed that with O 2 -containing gas, hydrogen chloride, which is an indicator of the deterioration phenomenon of the COSORB solution, continues to be generated, and with gas that does not contain O 2 , hydrogen chloride is not generated. Therefore, after removing O 2 in the mixed gas
I came to believe that these troubles could be eliminated by supplying the COSORB process, but as a result of various considerations, I found that 3.
If the raw material gas contains O 2 less than % by volume,
It has been found that by using the catalyst specified in the present invention, it is possible to easily reduce the amount by volume to 100 ppm or less, and depending on the conditions, to 10 to 1 ppm or less, and the intended purpose can be achieved. Also, the raw material gas
Before feeding to the COSORB process
Purified CO to remove O2 below 100ppm
The secondary effect is that the O 2 concentration inside is also reduced and the purity of purified CO is improved. Furthermore, the catalyst used in the present invention is copper-based or has a binary composition of copper and other metals such as zinc, manganese, chromium, nickel, etc., and has particularly excellent reaction activity and reaction selectivity, and is compatible with COSORB solutions. extremely harmful
40-60% in terms of ability to adsorb and remove impurity gases such as H2S
Copper oxide/60-40% zinc oxide is optimal. below
Further explanation will be given focusing on the O 2 removal process. A mixed gas containing CO as the main component and less than 3% by volume of O 2 is fed into the deoxidizer filled with the above catalyst.
When introduced at 10-80℃, preferably 20-50℃,
O 2 becomes mainly CO 2 and O 2 is removed. CO + 1/2O 2 → CO 2 In the present invention, it has been stated that the upper limit of O 2 content is 3% by volume, but as a practical matter, the amount of O 2 in converter gas or blast furnace gas will not exceed 3% by volume. In practical terms, it can be considered unlimited. Even when a catalyst is used, there is a problem of reaction selectivity like other general catalytic reactions, and reactions such as H 2 + 1/2O 2 → H 2 O 3H 2 + CO → H 2 O + CH 4 may proceed. If the gender is even 1%
Since H 2 O degrades the COSORB solution, it is necessary to dehumidify it in a later step. The catalyst specified by the present invention has very high low-temperature activity and reaction selectivity for CO + 1/2O 2 → CO 2 , but it also has a high reaction selectivity for the side reaction H 2 + 1/2O 2 →
In order to suppress reactions such as H 2 O as much as possible, it is better to lower the inlet gas temperature in the deoxidizer, which is 80℃.
Hereinafter, it is better to introduce the O 2 -containing gas preferably at a temperature below 50°C. Cu-based catalysts are also used as methanol synthesis catalysts, so the following reaction may occur: CO+2H 2 →CH 3 OH 2CO+4H 2 →CH 3 OCH 3 +H 2 O 2CO+2H 2 →CH 3 COOH. It is assumed that deterioration of COSORB solution due to oxygen-containing organic compounds occurs. Therefore, it is preferable to keep the outlet temperature of the deoxidizer at 230°C or lower, and the O2 - containing gas introduced into the deoxidizer is
Serve at 80°C, preferably 20-50°C. When the O 2 concentration is high, install a cooler etc. inside the deoxidizer to keep the outlet temperature below 230℃.
It is desirable that the content of oxygen-containing organic compounds be 50 ppm or less, preferably 10 ppm or less. Methanol etc. can be removed in the same way as water using an adsorption tower filled with synthetic zeolite etc., but methanol etc. decomposes because the temperature is raised during regeneration of the adsorption tower.
There is a possibility that carbon precipitation may occur or a chemical reaction may occur with the synthetic zeolite, resulting in no longer being desorbed. Therefore, it is desirable that the concentration of oxygen-containing organic compounds at the outlet of the oxygen absorber is 50 volume ppm or less. Thus reducing the O2 content to 100 ppm by volume, preferably 10 ppm
The mixed gas reduced to below is supplied to the COSORB process after dehumidification and demethanolization as required.
The reason why the O 2 content is set to 100 ppm or less by volume is as follows. That is, based on the above test results, the relationship between the O 2 concentration of the O 2 -containing gas in the COSORB solution and the rate of liquid deterioration is shown in Table 2, where the life of the solution at the same O 2 concentration is expressed in correspondence.
【表】
例えば、含O2ガス中のO2濃度が0.5%の時は
COSORB溶液の使用(寿命)年数は約1年しか
ないが、少なくともO2濃度を100ppm以下にする
と液の使用年数は約3年となり、経済的に合理的
になる。当然、O2濃度が低くなればなるほど液
寿命は長くなり、特に10ppm以下にすると約7年
となり、使用上、問題が無くなる。又1ppm以下
では15年以上の液寿命となる。
[実施例]
第1図および第2図は本発明の実施例を示すフ
ロー図である。CO:68%、CO2:16%、N2:
13.5%、H2:2%、O2:0.5%、その他の微量不
純物を含んだCOを主成分とする含O2ガスである
LDG(転炉ガス:40℃)を圧縮機1(油入りスク
リユーコンプレツサーあるいはオイルフリーコン
プレツサー)にて1〜100Kg/cm2G例えば3Kg/
cm2Gまで圧縮した後熱交換器2を通して40℃まで
冷却し、凝縮水をドレーン3によつて排水した
後、予備脱湿装置Aに通す。予備脱湿装置Aに導
入されたLDGは熱交換器4および5で冷却され、
生成した凝縮水はドレーン6によつて排水され
る。特に熱交換器5ではブラインにより露点温度
2〜8℃まで冷却されるので脱湿効果が大きい。
ここで予備的に脱湿するのは脱湿の負荷分散すな
わち最終脱湿の負荷を軽減する及び、下流工程の
充填層での水凝縮等を防止するため、及び下流活
性炭塔で水蒸気が多く存在すると能力が低下する
ためであり、場合によつては省略することもでき
る。次に2〜8℃まで冷却されたLDGは熱交換
器4にて25℃まで加温され、活性炭および酸添
着・アルカリ添着活性炭を充填した充填塔7,8
を通す。充填塔7は圧縮機2として油入りスクリ
ユーコンプレツサーを使用した場合の油除去を目
的としたものであり圧縮機2がオイルフリーコン
プレツサーであれば充填塔7は省略できる。次に
充填塔8ではLDG中に含まれる微量不純物であ
るH2S、HCN、SO4、NH3、CS2、HF等が除去
される。こうして脱湿および不純物除去された
LDGは250℃で銅系触媒(例えば50%Cu−50%
ZnO)を充填した反応塔(脱酸素装置)9を通過
してLDG中のO2がCO2に変換される。この際酸
化反応により125℃位まで温度が上昇するので熱
交換器10で常温まで冷却し脱湿装置Bを通す。
脱湿装置Bは例えば合成ゼオライト等が充填され
た充填塔11,11′よりなり、水分を1容量
ppm以下に脱湿する。次いでLDGはCOSORBプ
ロセスに供給されCOの精製がおこなわれる。
また脱湿装置BではCO+H2→CH3OH、或は
H2+1/2O2→H2Oの反応によつて生成される
CH3OHやH2Oも除去される。なお反応塔9での
反応が実質上CO+1/2O2→CO2のみに極限される
様な場合は、第2図のフロー図に示すように脱湿
装置Bを反応塔9の前に設置してこれを最終脱湿
装置としても良い。尚13,14はフイルター、
熱交換器2,10は冷却水によるものである。
以上のようにして得られたLDGはO2濃度が1
容量ppm以下、メタノール等の含酸素有機化合物
の濃度がガスクロマトグラフの定量下限以下、ま
たH2とO2によるH2Oの生成は含有O2に対する選
択率として1%以下であることが確認された。こ
のLDGをCOSORBプロセスに導入してCOの精製
を行なつたところ、第3表に実施例として示す結
果が得られた。O2を除去しないものを比較例と
して併記する。[Table] For example, when the O 2 concentration in O 2- containing gas is 0.5%,
The COSORB solution has a service life of only about one year, but if the O 2 concentration is at least 100 ppm or less, the solution can be used for about three years, which makes it economically reasonable. Naturally, the lower the O 2 concentration, the longer the liquid life will be, especially if it is 10 ppm or less, it will be about 7 years, and there will be no problems in use. Also, if the concentration is less than 1 ppm, the liquid life will be more than 15 years. [Embodiment] FIGS. 1 and 2 are flow diagrams showing an embodiment of the present invention. CO: 68%, CO2 : 16%, N2 :
13.5%, H2 : 2%, O2 : 0.5%, and O2- containing gas whose main component is CO, containing other trace impurities.
LDG (converter gas: 40℃) is compressed by compressor 1 (oil-filled screw compressor or oil-free compressor) to 1 to 100Kg/cm 2 G, for example 3Kg/
After being compressed to cm 2 G, it is cooled to 40° C. through a heat exchanger 2, and after draining the condensed water through a drain 3, it is passed through a preliminary dehumidification device A. LDG introduced into the preliminary dehumidifier A is cooled by heat exchangers 4 and 5,
The generated condensed water is drained through a drain 6. In particular, in the heat exchanger 5, the brine cools down to a dew point temperature of 2 to 8°C, so the dehumidification effect is large.
The purpose of preliminary dehumidification here is to distribute the dehumidification load, i.e. to reduce the final dehumidification load, to prevent water condensation in the packed bed in the downstream process, and to prevent the presence of a large amount of water vapor in the downstream activated carbon tower. This is because the performance will decrease, and it may be omitted in some cases. Next, the LDG cooled to 2 to 8 degrees Celsius is heated to 25 degrees Celsius in a heat exchanger 4, and packed towers 7 and 8 filled with activated carbon and acid-impregnated/alkali-impregnated activated carbon.
Pass through. The purpose of the packed tower 7 is to remove oil when an oil-filled screw compressor is used as the compressor 2, and if the compressor 2 is an oil-free compressor, the packed tower 7 can be omitted. Next, in the packed column 8, trace impurities such as H 2 S, HCN, SO 4 , NH 3 , CS 2 , HF, etc. contained in the LDG are removed. This dehumidifies and removes impurities.
LDG is heated with a copper-based catalyst (e.g. 50% Cu - 50%
O 2 in LDG is converted to CO 2 by passing through a reaction tower (deoxygenation device) 9 filled with ZnO). At this time, the temperature rises to about 125° C. due to the oxidation reaction, so it is cooled down to room temperature by a heat exchanger 10 and passed through a dehumidifier B.
The dehumidifier B consists of packed towers 11 and 11' filled with, for example, synthetic zeolite, etc., and removes water by one volume.
Dehumidify to below ppm. LDG is then fed to the COSORB process to purify CO. In addition, in dehumidification equipment B, CO + H 2 → CH 3 OH, or
Produced by the reaction H 2 + 1/2O 2 →H 2 O
CH 3 OH and H 2 O are also removed. If the reaction in reaction tower 9 is substantially limited to CO + 1/2O 2 → CO 2 , install dehumidifier B in front of reaction tower 9 as shown in the flow diagram of Figure 2. This may also be used as a final dehumidification device. Note that 13 and 14 are filters,
The heat exchangers 2 and 10 are based on cooling water. The LDG obtained as above has an O 2 concentration of 1
It was confirmed that the volume was less than ppm, the concentration of oxygen-containing organic compounds such as methanol was less than the lower limit of gas chromatography quantification, and the production of H 2 O by H 2 and O 2 was less than 1% as a selectivity to the O 2 contained. Ta. When this LDG was introduced into the COSORB process to purify CO, the results shown in Table 3 as examples were obtained. A comparison example that does not remove O 2 is also shown.
【表】
上記より、含O2ガスから、O2を除去した後、
COSORBプロセスに供給すると、COSORB溶液
の劣化速度が、極端に抑制されることが、確認で
きた。
[発明の効果]
以上のように本発明によれば、COを主成分と
しO2を含有する混合ガス中のO2を事前に一定濃
度以下に取り除くことによつてCOSORBプロセ
スのCOSORB溶液の劣化および熱交換器の閉塞
を防うことができCOSORBプロセスの長期安定
運転が可能となる。[Table] From the above, after removing O 2 from O 2 - containing gas,
It was confirmed that when supplied to the COSORB process, the deterioration rate of the COSORB solution was extremely suppressed. [Effects of the Invention] As described above, according to the present invention, deterioration of the COSORB solution in the COSORB process can be prevented by removing O 2 in the mixed gas containing O 2 as a main component to a certain concentration in advance. This also prevents clogging of the heat exchanger and enables long-term stable operation of the COSORB process.
第1図、第2図は本発明の実施例を示すフロー
図、第3図および第4図はガス吹込み量と塩化水
素発生速度との関係図である。
1……圧縮機、2,4,5,10……熱交換
器、3,6……ドレーン、7,8,11,11′
……充填塔、9……反応塔、13,14……フイ
ルター、A……予備脱湿装置、B……脱湿装置。
FIGS. 1 and 2 are flowcharts showing an embodiment of the present invention, and FIGS. 3 and 4 are diagrams showing the relationship between the amount of gas blown and the rate of hydrogen chloride generation. 1... Compressor, 2, 4, 5, 10... Heat exchanger, 3, 6... Drain, 7, 8, 11, 11'
... Packed tower, 9 ... Reaction tower, 13, 14 ... Filter, A ... Preliminary dehumidification device, B ... Dehumidification device.
Claims (1)
する混合ガスを、少なくとも銅を含有する触媒の
充填された脱酸素装置に80℃以下で導入し、主と
してO2をCO2に変換することによつてO2含有量
を100容量ppm以下に低下させてから、金属錯塩
の芳香族炭化水素溶液に供給してCOの精製を行
うことを特長とするCOの精製方法。1 A mixed gas containing CO as the main component and 3% by volume or less of O 2 is introduced at 80°C or below into a deoxidizer packed with a catalyst containing at least copper, converting mainly O 2 to CO 2 A method for purifying CO, which comprises reducing the O 2 content to 100 ppm or less by volume, and then supplying the metal complex salt to an aromatic hydrocarbon solution to purify CO.
Priority Applications (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61098509A JPS62256708A (en) | 1986-04-28 | 1986-04-28 | Method for purifying co |
| AU72116/87A AU586333B2 (en) | 1986-04-28 | 1987-04-27 | Method of purifying CO |
| DE19873714126 DE3714126A1 (en) | 1986-04-28 | 1987-04-28 | Process for purifying CO |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61098509A JPS62256708A (en) | 1986-04-28 | 1986-04-28 | Method for purifying co |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS62256708A JPS62256708A (en) | 1987-11-09 |
| JPH048368B2 true JPH048368B2 (en) | 1992-02-14 |
Family
ID=14221616
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP61098509A Granted JPS62256708A (en) | 1986-04-28 | 1986-04-28 | Method for purifying co |
Country Status (3)
| Country | Link |
|---|---|
| JP (1) | JPS62256708A (en) |
| AU (1) | AU586333B2 (en) |
| DE (1) | DE3714126A1 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4746111B2 (en) * | 2009-02-27 | 2011-08-10 | 三菱重工業株式会社 | CO2 recovery apparatus and method |
Family Cites Families (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US2031475A (en) * | 1931-06-25 | 1936-02-18 | Joseph C W Frazer | Oxidizing catalysts |
| US3776972A (en) * | 1972-06-02 | 1973-12-04 | Exxon Research Engineering Co | Ligand complexes of cu(i)salts |
| DE3017998C2 (en) * | 1980-05-10 | 1994-05-26 | Krupp Koppers Gmbh | Process for the catalytic treatment of partial oxidation raw gas |
| JPS57145018A (en) * | 1981-03-04 | 1982-09-07 | Babcock Hitachi Kk | Separating and concentrating method of carbon monoxide |
| DE3243206A1 (en) * | 1982-11-23 | 1984-05-24 | Basf Ag, 6700 Ludwigshafen | METHOD FOR PURIFYING CO AND / OR CO (DOWN ARROW) 2 GASES CONTAINING (DOWN ARROW) |
| US4508694A (en) * | 1983-05-06 | 1985-04-02 | Exxon Research & Engineering Co. | Separation and recovery of carbon monoxide by copper (I) complexes |
| JPS60151207A (en) * | 1984-01-20 | 1985-08-09 | Mitsubishi Heavy Ind Ltd | Separation of carbon monoxide |
| JPS60161317A (en) * | 1984-01-31 | 1985-08-23 | Kansai Coke & Chem Co Ltd | Method for removing oxygen from oxygen-containing gas consisting essentially of carbon monoxide |
| JPS60187336A (en) * | 1984-03-05 | 1985-09-24 | Chiyoda Chem Eng & Constr Co Ltd | carbon monoxide absorbent |
-
1986
- 1986-04-28 JP JP61098509A patent/JPS62256708A/en active Granted
-
1987
- 1987-04-27 AU AU72116/87A patent/AU586333B2/en not_active Ceased
- 1987-04-28 DE DE19873714126 patent/DE3714126A1/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| AU586333B2 (en) | 1989-07-06 |
| AU7211687A (en) | 1987-11-12 |
| DE3714126C2 (en) | 1989-08-03 |
| JPS62256708A (en) | 1987-11-09 |
| DE3714126A1 (en) | 1987-10-29 |
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