JPH0243917A - Removal of carbon dioxide - Google Patents

Removal of carbon dioxide

Info

Publication number
JPH0243917A
JPH0243917A JP63192104A JP19210488A JPH0243917A JP H0243917 A JPH0243917 A JP H0243917A JP 63192104 A JP63192104 A JP 63192104A JP 19210488 A JP19210488 A JP 19210488A JP H0243917 A JPH0243917 A JP H0243917A
Authority
JP
Japan
Prior art keywords
adsorbent
carbon dioxide
adsorption
amount
molded body
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.)
Granted
Application number
JP63192104A
Other languages
Japanese (ja)
Other versions
JP2651603B2 (en
Inventor
Fushinobu Asano
浅野 節信
Kenji Otsuka
健二 大塚
Noboru Takemasa
登 武政
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.)
Japan Pionics Ltd
Original Assignee
Japan Pionics 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 Japan Pionics Ltd filed Critical Japan Pionics Ltd
Priority to JP63192104A priority Critical patent/JP2651603B2/en
Publication of JPH0243917A publication Critical patent/JPH0243917A/en
Application granted granted Critical
Publication of JP2651603B2 publication Critical patent/JP2651603B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/043Carbonates or bicarbonates, e.g. limestone, dolomite, aragonite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/024Compounds of Zn, Cd, Hg
    • B01J20/0244Compounds of Zn
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/0203Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
    • B01J20/0274Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04 characterised by the type of anion
    • B01J20/0277Carbonates of compounds other than those provided for in B01J20/043
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • B01J20/08Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28002Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
    • B01J20/28011Other properties, e.g. density, crush strength
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/3007Moulding, shaping or extruding
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/3078Thermal treatment, e.g. calcining or pyrolizing
    • 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

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  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Treating Waste Gases (AREA)
  • Separation Of Gases By Adsorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PURPOSE:To enhance the removal efficiency of CO2 by bringing CO2-containing gas into contact with an adsorbent composed of a molded body formed from a composition prepared by mixing zinc oxide, aluminum oxide and an alkali compound. CONSTITUTION:Basic zinc carbonate, aluminum oxide and anhydrous potassium carbonate or sodium bicarbonate are mixed, molded, dried and baked to obtain a molded body composed of a composition wherein zinc oxide, aluminum oxide and an alkali compound are mixed. This molded body is brought into contact with CO2-containing gas as an adsorbent to adsorb and remove CO2. CO2 is desorbed from the adsorbent by heating. By using this adsorbent, CO2 removal efficiency is enhanced.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は二酸化炭素の除去方法に関し、さらに詳細には
、二酸化炭素の除去性能が高く、がっ、成型体強度の優
れた吸着剤を用いた二酸化炭素の除去方法に関する。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a method for removing carbon dioxide, and more specifically, the present invention relates to a method for removing carbon dioxide, and more specifically, a method using an adsorbent that has high carbon dioxide removal performance and excellent molded body strength. This paper relates to a method for removing carbon dioxide.

水素、窒素、ヘリウム、アルゴンおよび酸素などのガス
はボンベ詰めあるいは液化状態で市販され、各種工業用
および学術用どして使用されている。
Gases such as hydrogen, nitrogen, helium, argon, and oxygen are commercially available in cylinders or in liquefied form, and are used for various industrial and academic purposes.

近年、半導体製造プロセス、光フアイバー製造プロセス
、金属の熱処理プロセスおよび分析などの分野における
技術の高度化に伴い、これらのガスも高純度であること
が要求されている。
In recent years, with the advancement of technology in fields such as semiconductor manufacturing processes, optical fiber manufacturing processes, metal heat treatment processes, and analysis, these gases are also required to have high purity.

〔従来の技術〕[Conventional technology]

高純度ガスを得るためにガス中に含有される不純物の種
類などに応じて種々な精製方法が知られており、水素、
炭化水素、−酸化炭素などの不純物については、これら
を燃焼させて二酸化炭素および/または水に転換し、元
から混入していた二酸化炭素および水などとともに吸着
剤に接触させてこれらを除去する方法が用いられている
Various purification methods are known to obtain high-purity gas depending on the type of impurities contained in the gas.
A method for removing impurities such as hydrocarbons and carbon oxides by burning them and converting them into carbon dioxide and/or water, and then contacting them with an adsorbent along with the carbon dioxide and water that were originally mixed in. is used.

これらの吸着剤としては合成ゼオライトが一般的に広く
用いられ、例えばモレキュラーシーブ(米国、ユニオン
カーバイド社)が最もよく知られている。不純物を吸着
した吸着剤は高温で再生することにより繰り返し使用さ
れる。
Synthetic zeolites are generally widely used as these adsorbents, and for example, Molecular Sieve (Union Carbide, USA) is the most well-known. The adsorbent that has adsorbed impurities can be used repeatedly by regenerating it at high temperature.

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

半導体の集積度が高くなり、これにともなってガスの純
度も向上し、不純物の濃度が低くなる方向にあるが、さ
らに不純物を除くことが要求されている。一方、半導体
プロセスなどにおいては設置スペースなどの関係から装
置の小型化も強く要望されている。
As the degree of integration of semiconductors increases, the purity of gases also improves, and the concentration of impurities tends to decrease, but there is a need to further remove impurities. On the other hand, in semiconductor processes and the like, there is a strong demand for downsizing of equipment due to installation space and other considerations.

現在多く用いられているモレキュラーシーブ5Aについ
て低濃度の二酸化炭素の平衡吸着量を測定すると、二酸
化炭素の濃度がlppmのような低濃度の場合には、二
酸化炭素濃度が10ppmのときの約177に低下する
。すなわち、同量のガスを精製するためには濃度が1/
10に低下しても吸着筒の容積は7/10にしか小さく
ならない。
When measuring the equilibrium adsorption amount of carbon dioxide at low concentrations using Molecular Sieve 5A, which is currently widely used, it is found that when the concentration of carbon dioxide is as low as lppm, it is about 177 compared to when the carbon dioxide concentration is 10 ppm. descend. In other words, in order to purify the same amount of gas, the concentration must be 1/
Even if it is reduced to 10, the volume of the adsorption column will only be reduced to 7/10.

吸着筒をさらに小さくするには加熱再生のサイクルを短
くするか、あるいは吸着温度をO′C以下のような低温
に下げるなどで吸着量の増大を図る必要がある。
In order to further reduce the size of the adsorption column, it is necessary to increase the amount of adsorption by shortening the heating regeneration cycle or lowering the adsorption temperature to a low temperature below O'C.

しかしながら、加熱サイクルを短くするにも設計上限度
があり、また、吸着温度を下げる場合にはチラーや冷凍
機などの設置が必要となり、小型化の要求には対応でき
なくなるという欠点がある。
However, there is a design upper limit for shortening the heating cycle, and lowering the adsorption temperature requires the installation of a chiller, refrigerator, etc., which has the drawback of not being able to meet demands for miniaturization.

これに対し、本発明者らは先に、低濃度においても二酸
化炭素を効率良く除去するものとして酸化亜鉛を主成分
とする成型体を吸着剤として使用する方法を見い出した
(特願昭62−318800号)。この方法はモレキュ
ラーシーブなどを用いる方法に比べて吸着性能が高く、
特に冷却手段を用いることもなく二酸化炭素を効率良く
除去することができ、また、比較的低い温度で吸着剤の
再生が出来るという利点を有している。
In contrast, the present inventors have previously discovered a method of using a molded body containing zinc oxide as a main component as an adsorbent to efficiently remove carbon dioxide even at low concentrations (Japanese Patent Application No. 1983- No. 318800). This method has higher adsorption performance than methods using molecular sieves, etc.
In particular, it has the advantage that carbon dioxide can be efficiently removed without using any cooling means, and that the adsorbent can be regenerated at a relatively low temperature.

しかしながら、この吸着剤を用いても吸着筒を小型化す
るには、未だ吸着性能が充分とはいえず、また、不純物
を吸着した吸着剤は加熱再生により繰り返し使用される
が、このときの落圧およびパージ工程などにおいて、条
件によっては粉塵が発生し、これが精製ガス中に混入す
る虞れのあることも判明した。
However, even if this adsorbent is used, the adsorption performance is still not sufficient to downsize the adsorption column, and the adsorbent that has adsorbed impurities is repeatedly used by heating and regenerating, but the droplets at this time are It was also discovered that dust may be generated depending on the conditions during the pressure and purge steps, and there is a risk that this dust may be mixed into the purified gas.

〔課題を解決するための手段、作用〕[Means and actions for solving problems]

本発明者らは、さらに吸着性能が高く、しかも粉末の混
入などの虞れのない除去方法を得るべく研究を続けた結
果、酸化亜鉛に酸化アルミニウムおよびアルカリ化合物
を加えた組成物の成型体を用いることにより、粉塵の発
生がなく、かつ、二酸化炭素をさらに効率良く除去しう
ろことを見い出し本発明を完成した。
The present inventors continued their research to find a removal method that has even higher adsorption performance and is free from the risk of powder contamination. As a result, they developed a molded body of a composition in which aluminum oxide and an alkali compound were added to zinc oxide. They have discovered that by using scales, no dust is generated and carbon dioxide can be removed more efficiently, and the present invention has been completed.

すなわち、本発明は不純物として二酸化炭素を含有する
ガスを吸着剤と接触させて、当該ガスから二酸化炭素を
除去する二酸化炭素の除去方法において、吸着剤として
酸化亜鉛、酸化アルミニウムおよびアルカリ化合物を混
合してなる組成物の成型体を用いることを特徴とする二
酸化炭素の除去方法である。
That is, the present invention provides a carbon dioxide removal method in which a gas containing carbon dioxide as an impurity is brought into contact with an adsorbent to remove carbon dioxide from the gas. A method for removing carbon dioxide characterized by using a molded body of a composition comprising:

本発明は水素、窒素、ヘリウム、アルゴンおよび酸素な
どのガス中に不純物として含有される二酸化炭素の除去
に適用される。また、これらのガス中に水分が含有され
るときには水分も同時に除去される。
The present invention is applied to the removal of carbon dioxide contained as an impurity in gases such as hydrogen, nitrogen, helium, argon and oxygen. Moreover, when moisture is contained in these gases, the moisture is also removed at the same time.

本発明で使用される吸着剤は酸化亜鉛、酸化アルミニウ
ムおよびアルカリ化合物を用いたものである。
The adsorbent used in the present invention uses zinc oxide, aluminum oxide, and an alkali compound.

酸化亜鉛としては市販品の中から適当なものを選択して
もよく、また、焼成などによって酸化亜鉛に変化しうる
炭酸亜鉛、塩基性炭酸亜鉛、水酸化亜鉛および有機酸亜
鉛などの前駆物質を用いてもよい。
As zinc oxide, an appropriate one may be selected from commercially available products, and precursors such as zinc carbonate, basic zinc carbonate, zinc hydroxide, and organic acid zinc that can be converted to zinc oxide by calcination etc. May be used.

また、酸化アルミニウムは、通常はアルミナ水和物が使
用され、例えば市販のアルミナゾルあるいはこれを粉末
にした高濃度アルミナなどが好適である。
Further, as aluminum oxide, alumina hydrate is usually used, and for example, commercially available alumina sol or highly concentrated alumina made from powdered alumina sol is suitable.

さらに、アルカリ化合物としてはリチウム、ナトリウム
、カリウムなどのアルカリ金属およびアンモニウムの水
酸化物、炭□酸塩、重炭酸塩および酢酸塩などである。
Further, alkaline compounds include hydroxides, carbonates, bicarbonates, and acetates of alkali metals such as lithium, sodium, potassium, and ammonium.

これらのうちでも炭酸カリウム、重炭酸カリウム、水酸
化カリウム、炭酸ナトリウム、重炭酸ナトリウム、水酸
化ナトリウム、水酸化アンモニウムおよびこれらの混合
物などが好ましい。
Among these, potassium carbonate, potassium bicarbonate, potassium hydroxide, sodium carbonate, sodium bicarbonate, sodium hydroxide, ammonium hydroxide, and mixtures thereof are preferred.

酸化亜鉛に対する酸化アルミニウムおよびアルカリ化合
物の量は、亜鉛l原子数に対し、通常はアルミニウム0
.02〜0,60原子、好ましくは0.05〜0.40
原子であり、また、アルカリ化合物の量は、通常はアル
カリ金属またはアンモニウム基で0.02〜0.70原
子、好ましくは0.05〜0.50原子である。
The amount of aluminum oxide and alkali compounds relative to zinc oxide is usually 0% aluminum per 1 atomic number of zinc oxide.
.. 02-0.60 atoms, preferably 0.05-0.40
and the amount of alkali compound is usually 0.02 to 0.70 atoms, preferably 0.05 to 0.50 atoms of alkali metal or ammonium groups.

アルミニウムの原子比が0.02よりも小さいと成型体
の強度が低下する虞れがあり、一方、0゜60よりも大
きくなると炭酸ガスの吸着能力が低下する虞れがある。
If the atomic ratio of aluminum is less than 0.02, the strength of the molded product may decrease, while if it exceeds 0.60, the carbon dioxide adsorption ability may decrease.

また、アルカリ金属またはアンモニウム基の原子比が0
.02よりも小さくなると成型体の強度および吸着能力
が低下し、−方、0.70よりも大きくなると成型が難
しくなる。 吸着剤の調製方法としては、例えば亜鉛の
酸化物または酸化物の前駆物質とアルミナゾルおよびア
ルカリ化合物の混合物に水を加えて混練するか、あるい
は酸化亜鉛またはその前駆物質とアルミナゾルに水を加
えて練った後、さらにアルカリ化合物を加えて得なケー
キを成型する。
Also, the atomic ratio of alkali metal or ammonium groups is 0
.. If it is smaller than 0.02, the strength and adsorption capacity of the molded product will decrease, and if it is larger than 0.70, it will be difficult to mold. The adsorbent can be prepared by, for example, adding water to a mixture of zinc oxide or oxide precursor, alumina sol, and an alkali compound and kneading it, or adding water to zinc oxide or its precursor and alumina sol and kneading it. After that, an alkaline compound is further added to form a fine cake.

成型方法には種々の方法があり、例えば■上記で得た混
合物のケーキを押し出し成型し、得られたペレットを乾
燥する方法、■ケーキを乾燥した後粉砕し、これにグラ
ファイトなどの滑剤を添加、混合したものを打錠成型す
る方法、 ■ケーキを造粒機などを用いて、か粒状とする方法など
がある。
There are various molding methods, such as: ■ extrusion molding the cake of the mixture obtained above and drying the resulting pellets, ■ drying the cake, then crushing it, and adding a lubricant such as graphite to it. There are two methods: 1) forming a mixture into tablets, and 2) forming a cake into granules using a granulator.

これらのうちでは加工性および形状、大きさの選択の容
易さなどから押し出し成型により、ペレット状とするの
が一般的に便利であり、また、ペレットはマルメライザ
ーなどを用いてその端部をまるめな形とすることが好ま
しい。
Among these, it is generally convenient to make pellets by extrusion molding for ease of processing and selection of shape and size. It is preferable to have a shape.

成型体は空気または目的の精製ガスを流しながら180
〜600℃、好ましくは210〜450℃で焼成するこ
とにより吸着剤とされる。
The molded body is heated at 180°C while flowing air or the target purified gas.
It is made into an adsorbent by firing at ~600°C, preferably 210~450°C.

成型体の大きさおよび形状には特に制限はないが、球形
、円柱形、および円筒形などが代表例として挙げられる
。その大きさは球形であれば直径0.5〜10mm、円
柱形であれば直径0.5〜10mm、高さ2〜20mm
程度とされ、粒状など不定形のものであれば、ふるいの
目の開きで0.84〜5 、66mm程度の範囲のもの
が使用される。
There are no particular restrictions on the size and shape of the molded body, but representative examples include spherical, cylindrical, and cylindrical shapes. The size is 0.5 to 10 mm in diameter if spherical, 0.5 to 10 mm in diameter and 2 to 20 mm in height if cylindrical.
If the material is irregularly shaped, such as granules, a sieve with an opening of about 0.84 to 5.66 mm is used.

本発明で用いる成型体の密度は通常は0.5〜3.0g
/vtΩ、好丈しくは0.7〜2.5g/yyd2の範
囲である。本発明において密度とは成型体(粒)の重さ
を成型体の幾何学的体積で割ったものをいう。
The density of the molded product used in the present invention is usually 0.5 to 3.0 g.
/vtΩ, preferably in the range of 0.7 to 2.5 g/yyd2. In the present invention, density refers to the weight of a molded body (grains) divided by the geometric volume of the molded body.

また、成型体を吸着筒に充填した場合の充填密度は通常
は0.4〜2.0g/−好ましくは0.5〜15g/―
とされる。
In addition, the packing density when the molded body is packed into an adsorption column is usually 0.4 to 2.0 g/- preferably 0.5 to 15 g/-
It is said that

本発明において吸着剤は通常は吸着筒に充填され、これ
に二酸化炭素を含有するガスを通し両者を接触させるこ
とによってガス中の二酸化炭素が吸着除去される。この
ときガス中に水分が含有されるときにはこの水分も同時
に除去されて露点の低い精製ガスが得られる。
In the present invention, the adsorbent is usually packed in an adsorption column, and by passing a gas containing carbon dioxide through the adsorbent and bringing them into contact, carbon dioxide in the gas is adsorbed and removed. At this time, if water is contained in the gas, this water is also removed at the same time to obtain purified gas with a low dew point.

吸着温度は一般的には低いほうが好ましいが、80℃程
度以下であればよく、通常は60℃以下の常温で充分な
吸着性能を有し、特に冷却を必要としない。
Although the lower the adsorption temperature, the lower the adsorption temperature is generally preferred, it is sufficient as long as it is about 80°C or less, and usually has sufficient adsorption performance at room temperature of 60°C or less, and does not particularly require cooling.

接触時のガスの速度は合成ゼオライトを用いる場合と同
じ程度でよく通常は空筒線速度で150cm/sec以
下、好ましくは 1〜70cm/secとされる。また
、接触時の圧には特に制限はないが実用上は1〜10K
g/cm2Gの範囲で行われることが多い。
The gas velocity at the time of contact may be about the same as when using synthetic zeolite, and usually the cylinder linear velocity is 150 cm/sec or less, preferably 1 to 70 cm/sec. In addition, there is no particular limit to the pressure at the time of contact, but in practice it is 1 to 10K.
It is often carried out in the range of g/cm2G.

本発明において通常は二基の吸着筒が使用されガスの吸
着精製と吸着剤の加熱再生とが交互に切り替えられてお
こなわれる。二酸化炭素、水分などを吸着した吸着剤は
吸着筒に精製ガスを流しながら200〜500℃好まし
くは300〜400°Cで加熱することにより、二酸化
炭素、水などの不純物が脱着除去されて再生され、ガス
の吸着精製に繰り返し使用される。
In the present invention, two adsorption cylinders are normally used, and gas adsorption purification and adsorbent heating regeneration are alternately performed. The adsorbent that has adsorbed carbon dioxide, water, etc. is regenerated by desorbing and removing impurities such as carbon dioxide and water by heating it at 200 to 500°C, preferably 300 to 400°C while flowing purified gas through the adsorption column. , repeatedly used for adsorption purification of gases.

〔発明の効果〕〔Effect of the invention〕

本発明は、吸着剤として酸化亜鉛、酸化アルミニウムお
よびアルカリ化合物を混合してなる組成物の成型体を使
用することによって、従来用いられてきた合成ゼオライ
トによる方法に比ベて吸着性能が極めて高く、また、酸
化亜鉛のみを主成分とする成型体を用いた場合よりも吸
着量が高く、二酸化炭素を効率良く除去することが出来
る。
The present invention uses a molded composition made of a mixture of zinc oxide, aluminum oxide, and an alkali compound as an adsorbent, so that the adsorption performance is extremely high compared to the conventional method using synthetic zeolite. Furthermore, the amount of adsorption is higher than when using a molded body containing only zinc oxide as a main component, and carbon dioxide can be removed efficiently.

しかも吸着剤は比較的低い温度によって再生されるので
反復使用することが出来る。
Furthermore, the adsorbent can be regenerated at relatively low temperatures and thus can be used repeatedly.

また、成型体は充分な強度を有するので吸着筒に充填し
た状態で圧力を高圧から大気圧などに急激に下げたり、
温度を上下させるなど苛酷な条件で使用しても粉化する
ことがない。
In addition, since the molded product has sufficient strength, it is possible to rapidly reduce the pressure from high pressure to atmospheric pressure while filling the adsorption cylinder.
It will not turn into powder even when used under harsh conditions such as increasing or decreasing the temperature.

かくして精製ガス中に粉末が混入する虞がなく、また、
高吸着能を有するので、従来の方法に比べて装置も大巾
に小型化でき、半導体製造プロセスなどの限られたスペ
ースへの設置も容易となった。
In this way, there is no risk of powder being mixed into the purified gas, and
Because it has a high adsorption capacity, the device can be made much smaller than conventional methods, and it can be easily installed in limited spaces such as in semiconductor manufacturing processes.

〔実施例〕〔Example〕

実施例1 塩基性炭酸亜鉛500g、カタロイドAP(触媒化成■
製、高濃度アルミナ> 52.4g  (Zn 1原子
に対しAI 0.16原子)、無水炭酸カリウム30.
2g(Znl原子に対しK O,10原子)を小型ニー
ダ−に入れて3分間混合した後、水280gを加えて1
時間混練した。このケーキを小型押出機によって 1.
9φのノズル板より押出して得たペレットをマルメライ
ザーによって丸め、110℃にて2時間乾燥した。この
ものをマツフル炉に入れて350℃で1時間焼成するこ
とにより密度1.14g/mQ、充填密度0.74g/
−の吸着剤を得な。
Example 1 Basic zinc carbonate 500g, Cataloid AP (Catalyst Chemical ■
52.4 g of high-concentration alumina (0.16 atom of AI per 1 atom of Zn), 30 g of anhydrous potassium carbonate.
2g (KO, 10 atoms per Znl atom) was placed in a small kneader and mixed for 3 minutes, then 280g of water was added and 1
Kneaded for hours. This cake is processed using a small extruder.1.
The pellets obtained by extrusion through a 9φ nozzle plate were rolled into balls using a marmerizer and dried at 110° C. for 2 hours. This material was placed in a Matsufuru furnace and fired at 350°C for 1 hour, resulting in a density of 1.14 g/mQ and a packing density of 0.74 g/mQ.
- Obtain an adsorbent.

先ず、このものの粉化率を測定した。First, the powderization rate of this product was measured.

粉化率は約Logの吸着剤を精秤し、直径が80mmで
、20meshのふるいに入れて受皿と蓋を取り付けて
ストローク長55mm、280ストロ−先/minで5
分間水平に振とうし、受皿に落ちた粉の重量を秤り、次
式によって粉化率を求めた。
The pulverization rate was calculated by accurately weighing the adsorbent of approximately Log, placing it in a 20 mesh sieve with a diameter of 80 mm, attaching a saucer and a lid, and using a stroke length of 55 mm and 280 strokes/min for 5
The powder was shaken horizontally for a minute, the weight of the powder that fell into the saucer was weighed, and the powderization rate was determined using the following formula.

その結果、粉化率は0.6%であった。As a result, the powdering rate was 0.6%.

次に、吸着能の測定をおこなった。Next, the adsorption capacity was measured.

成型体を破砕して20〜32meshとしたちのIgを
Crush the molded body to 20-32 mesh and then add Ig.

内径7.53mm、長さ300 mmのステンレス製の
吸着筒内に充填し、これに精製済みの窒素を50mQ/
minで流しながら350℃で2時間再生しな。
A stainless steel adsorption column with an inner diameter of 7.53 mm and a length of 300 mm was filled with purified nitrogen at 50 mQ/
Regenerate at 350°C for 2 hours while running at min.

この吸着筒内に二酸化炭素10ppmを含有し、かつ露
点が一61°C(水分として9ppm)の原料窒素を、
圧力5Kg/cm2G、温度35℃、流jt1.8NZ
/minで出口の二酸化炭素濃度を原料ガス中の濃度の
0.95倍に達するまでの量測定した。
In this adsorption cylinder, raw nitrogen containing 10 ppm of carbon dioxide and having a dew point of 161°C (9 ppm as water) was
Pressure 5Kg/cm2G, temperature 35℃, flow jt1.8NZ
/min until the carbon dioxide concentration at the outlet reached 0.95 times the concentration in the raw material gas.

二酸化炭素の吸着量は次のようにして求めた吸着筒の出
口から出るガスを、FID−ガスクロマトグラフにより
分析した。ガスクロマトグラフの分離管がら出た二酸化
炭素を水素の存在下に600℃でニッケル触媒と接触さ
せてメタンに転換しな後FID (水素炎イオン化検出
器)に導いてそのメタン濃度を検出する。このようにし
て求めた出口の二酸化炭素濃度を時間軸に対してプロッ
トし、吸着筒の出口から出た二酸化炭素の量を求め、こ
の量を原料窒素中の二酸化炭素の量から差し引いた値を
二酸化炭素の吸着量とした。また、露点を浜田式露点計
にょって測定した。
The amount of carbon dioxide adsorbed was determined as follows, and the gas discharged from the outlet of the adsorption column was analyzed using an FID gas chromatograph. The carbon dioxide coming out of the separation tube of the gas chromatograph is brought into contact with a nickel catalyst at 600° C. in the presence of hydrogen to convert it into methane, and then introduced to an FID (Flame Ionization Detector) to detect the methane concentration. The carbon dioxide concentration at the outlet determined in this way is plotted against the time axis, the amount of carbon dioxide released from the outlet of the adsorption column is determined, and the value is calculated by subtracting this amount from the amount of carbon dioxide in the raw material nitrogen. It was taken as the amount of carbon dioxide adsorbed. Further, the dew point was measured using a Hamada dew point meter.

その結果、二酸化炭素の吸着量は、5.3mg/g吸着
剤であり、出口ガスの露点は一76°C(水分として1
ppm)であった。
As a result, the amount of carbon dioxide adsorbed was 5.3 mg/g of adsorbent, and the dew point of the outlet gas was -76°C (1 as moisture).
ppm).

続いてこの吸着剤の加熱再生試験をおこなった。上記の
二酸化炭素を吸着した吸着筒を、350°Cに加熱しな
がら精製窒素ガスを常圧下で流量50rd / min
で3時間流し、吸着剤から脱着した二酸化炭素量を前記
の測定方法で求めたところ5.1mg/g吸若剤であっ
た。
Subsequently, a heating regeneration test of this adsorbent was conducted. While heating the above carbon dioxide adsorbing cylinder to 350°C, purified nitrogen gas was supplied at a flow rate of 50rd/min under normal pressure.
The amount of carbon dioxide desorbed from the adsorbent was determined using the measurement method described above and was 5.1 mg/g of the absorbent.

さらに、この再生済みの吸着剤について、再度前記と同
じ条件で原料窒素を通して吸着実験を行ったところ二酸
化炭素の吸着量は5 、2mg/g吸着剤であった。
Furthermore, when this regenerated adsorbent was again subjected to an adsorption experiment under the same conditions as above by passing raw nitrogen through it, the amount of carbon dioxide adsorbed was 5.2 mg/g of the adsorbent.

実施例2 実施例1における原料窒素ガス中の二酸化炭素の濃度を
30.2pρmに代えた他は実施例1と同様にして二酸
化炭素の吸着量、再生時の脱着量および再吸着量を測定
しな。
Example 2 The amount of carbon dioxide adsorbed, the amount of desorption during regeneration, and the amount of re-adsorption were measured in the same manner as in Example 1, except that the concentration of carbon dioxide in the raw material nitrogen gas in Example 1 was changed to 30.2 ppm. Na.

その結果、吸着量は5.7mg/g吸着剤、脱着量は5
.7mg/g吸着剤、再吸着量は5.6mg/g吸着剤
であった。
As a result, the adsorption amount was 5.7 mg/g adsorbent, and the desorption amount was 5.7 mg/g adsorbent.
.. 7 mg/g adsorbent, and the re-adsorption amount was 5.6 mg/g adsorbent.

実施例3 実施例1における吸着温度および再吸着温度の35℃を
55℃に代えたほかは、実施例1と同様にして実験を行
った。
Example 3 An experiment was conducted in the same manner as in Example 1, except that the adsorption temperature and re-adsorption temperature in Example 1, 35°C, were changed to 55°C.

その結果、吸着量は4.9mg/g吸着剤、脱着量は4
.8mg/g吸着剤、再吸着量は4.6mg/g吸着剤
であった。
As a result, the adsorption amount was 4.9 mg/g adsorbent, and the desorption amount was 4.9 mg/g adsorbent.
.. 8 mg/g adsorbent, and the re-adsorption amount was 4.6 mg/g adsorbent.

実施例4および5 実施例1における窒素ガスの代わりに水素ガスを用いた
。二酸化炭素を]、0.2ppm  (実施例4)およ
び2.7ppm (実施例5)を含有する水素ガスのそ
れぞれについて実施例1におけると同様にして実験を行
った。
Examples 4 and 5 Hydrogen gas was used instead of nitrogen gas in Example 1. Experiments were conducted in the same manner as in Example 1 for hydrogen gas containing 0.2 ppm (Example 4) and 2.7 ppm (Example 5) of carbon dioxide], respectively.

その結果、実施例4については吸着量は8.2mg/g
吸着剤、脱着量は8.0mg/g吸着剤、再吸着量は8
.0mg/g吸着剤であり、実施例5については吸着量
は9.8mg/g吸着剤、脱着量は9.5mg/g吸着
剤、再吸着量は9.6mg/g吸着剤であった。
As a result, for Example 4, the adsorption amount was 8.2 mg/g.
Adsorbent, desorption amount is 8.0 mg/g adsorbent, re-adsorption amount is 8.
.. In Example 5, the amount of adsorption was 9.8 mg/g adsorbent, the amount of desorption was 9.5 mg/g adsorbent, and the amount of re-adsorption was 9.6 mg/g adsorbent.

実施例6 実施例1における窒素ガスの代わりに酸素ガスを用いた
。二酸化炭素を30ppmを含有する酸素ガスについて
実施例1におけると同様にして実験を行った。
Example 6 Oxygen gas was used instead of nitrogen gas in Example 1. An experiment was conducted in the same manner as in Example 1 using oxygen gas containing 30 ppm of carbon dioxide.

その結果、吸着量は4.9mg / g吸着剤、脱着量
は4.9+ng/ g吸着剤、再吸着量は5.0mg/
g吸着剤であった。
As a result, the amount of adsorption was 4.9 mg/g adsorbent, the amount of desorption was 4.9+ng/g adsorbent, and the amount of re-adsorption was 5.0 mg/g adsorbent.
g adsorbent.

実施例7 塩基性炭酸亜鉛782g、カタロイドA P 85.2
g(Zn 1原子に対しAI 0.16原子)、水34
1gを加えて90分混練した後、28%アンモニア水2
2.7g(Zn 1原子に対しN84基0 、047原
子〉を加えてさらに30分間混練した。このケーキを押
出し成型して得たベレットをマルメライザーで丸めた後
、実施例1におけると同じ条件で乾燥し、焼成して密度
が1.23g/d、充填密度0.80g/dの吸着剤を
得た。
Example 7 Basic zinc carbonate 782g, Cataloid AP 85.2
g (0.16 atoms of AI per 1 atom of Zn), water 34
After adding 1g and kneading for 90 minutes, add 28% ammonia water 2
2.7 g (0,047 atoms of N84 groups per 1 atom of Zn) was added and kneaded for an additional 30 minutes. The pellets obtained by extrusion molding this cake were rolled with a marmerizer, and then the same conditions as in Example 1 were applied. The adsorbent was dried and fired to obtain an adsorbent having a density of 1.23 g/d and a packing density of 0.80 g/d.

このものの粉化率を測定したところ0.1%であった。The pulverization rate of this product was measured and found to be 0.1%.

この吸着剤を用いて二酸化炭素10ppmを含有する窒
素ガスについて実施例1と同様にして実験を行った。
Using this adsorbent, an experiment was conducted in the same manner as in Example 1 using nitrogen gas containing 10 ppm of carbon dioxide.

その結果、吸着量は3.5mg/g吸着剤、脱着量は3
.4mg/g吸着剤、再吸着量は3.3mg/g吸着剤
であった。
As a result, the adsorption amount was 3.5 mg/g adsorbent, and the desorption amount was 3.5 mg/g adsorbent.
.. 4 mg/g adsorbent, and the re-adsorption amount was 3.3 mg/g adsorbent.

実施例8 活性酸化亜鉛79 、9g、カタロイドA P I2.
2g(Zn 1原子に対しAI 0.16原子)、水4
9.8gを加えて60分混練した後、重炭酸ナトリウム
8゜4g(Zn 1原子に対しNa 0.10原子)を
加えてさらに30分間混練した。このケーキを押出し成
型して得たベレットをマルメライザーで丸めな後、実施
例1におけると同じ条件で乾燥し、焼成して密度が1.
36g/m1ll、充填密度0.88g/ydの吸着剤
を得た。
Example 8 Active Zinc Oxide 79, 9g, Cataloid AP I2.
2g (0.16 atom of AI per 1 atom of Zn), 4g of water
After adding 9.8 g and kneading for 60 minutes, 8.4 g of sodium bicarbonate (0.10 atom of Na per 1 atom of Zn) was added and kneading was further continued for 30 minutes. The pellets obtained by extrusion molding this cake were rounded with a marmerizer, dried under the same conditions as in Example 1, and baked to a density of 1.
An adsorbent with a packing density of 36 g/ml and a packing density of 0.88 g/yd was obtained.

このものの粉化率を測定したところ0.3%であった。The powdering rate of this product was measured and found to be 0.3%.

この吸着剤を用いて二酸化炭素10ppmを含有する窒
素ガスについて実施例1と同様にして実験を行った。
Using this adsorbent, an experiment was conducted in the same manner as in Example 1 using nitrogen gas containing 10 ppm of carbon dioxide.

その結果、吸着量は5.0mg/g吸着剤、脱着量は4
.8mg/g吸着剤、再吸着量は4.9mg/g吸着剤
であった。
As a result, the amount of adsorption was 5.0 mg/g adsorbent, and the amount of desorption was 4.
.. 8 mg/g adsorbent, and the re-adsorption amount was 4.9 mg/g adsorbent.

実施例9 塩基性炭酸亜鉛782g、カタロイドA P I27.
8g(Zn 1原子に対しA10.24原子)、水37
5.4gを加えて50分混練した後、28%アンモニア
水213g (Zn 1原子に対しNH4基0.05原
子)を加えて20分間練り、次に重炭酸カリウム210
.2g(Zn 1原子に対しK O,30原子)を加え
てさらに20分間混練した。このケーキを押出し成型し
て得たベレットをマルメライザーで丸めた後、実施例1
におけると同じ条件で乾燥し、焼成して密度が1.93
g/d、充填密度1.25g/−の吸着剤を得た。
Example 9 Basic zinc carbonate 782g, Cataloid AP I27.
8g (10.24 atoms of A per 1 atom of Zn), 37% of water
After adding 5.4 g and kneading for 50 minutes, 213 g of 28% ammonia water (0.05 atom of NH4 group per 1 atom of Zn) was added and kneading for 20 minutes, and then 210 g of potassium bicarbonate was added.
.. 2 g (K 2 O, 30 atoms per 1 atom of Zn) was added and kneaded for an additional 20 minutes. Example 1
After drying and firing under the same conditions as in
An adsorbent with a packing density of 1.25 g/d and a packing density of 1.25 g/d was obtained.

このものの粉化率を測定したところ0.2%であった。The pulverization rate of this product was measured and was 0.2%.

この吸着剤を用いて二酸化炭素10ppmを含有する窒
素ガスについて実施例1と同様にして実験を行った。
Using this adsorbent, an experiment was conducted in the same manner as in Example 1 using nitrogen gas containing 10 ppm of carbon dioxide.

その結果、吸着量は3.2mg/g吸着剤、脱着量は2
.8mg/g吸着剤、再吸着量は2.9mg/g吸着剤
であった。
As a result, the adsorption amount was 3.2 mg/g adsorbent, and the desorption amount was 2.
.. The adsorption amount was 8 mg/g adsorbent and the re-adsorption amount was 2.9 mg/g adsorbent.

比較例1 モレキュラーシーブ5A(ユニオンカーバイド社製)を
20〜32meshに破砕した吸着剤を使用し、実施例
1と同様にしてテストをおこなったところ二酸化炭素の
吸着量はo、65mg/g吸着剤、再生によって脱着し
た二酸化炭素は帆59mg/g吸着剤、再吸着量は帆6
1mg/g吸着剤であった。
Comparative Example 1 A test was conducted in the same manner as in Example 1 using an adsorbent made by crushing Molecular Sieve 5A (manufactured by Union Carbide) into 20 to 32 mesh pieces, and the adsorption amount of carbon dioxide was 0, 65 mg/g adsorbent. , the carbon dioxide desorbed by regeneration is 59 mg/g of adsorbent, and the amount of re-adsorption is 6
1 mg/g adsorbent.

比較例2 塩基性炭酸亜鉛を300℃で焼成した市販の活性酸化亜
鉛82gとアルミナセメント18g混合し、51gの水
を加えて混練し、押出し成型して得たベレットをマルメ
ライザーで丸めた後、実施例1におけると同じ条件で乾
燥し、焼成して成型体を得た。
Comparative Example 2 82 g of commercially available activated zinc oxide prepared by baking basic zinc carbonate at 300°C and 18 g of alumina cement were mixed, 51 g of water was added and kneaded, and the pellet obtained by extrusion molding was rolled with a marmerizer. It was dried and fired under the same conditions as in Example 1 to obtain a molded body.

このものの粉化率は1.2%であった。The powdering rate of this product was 1.2%.

この成型体を20〜32meshに破砕し、実施例1に
おけると同様にして実験を行った。
This molded body was crushed into 20 to 32 meshes, and an experiment was conducted in the same manner as in Example 1.

その結果、吸着量は2.6mg/g 、脱着量は2.7
mg/g 、再吸着量は2.3mg/gであった。
As a result, the amount of adsorption was 2.6 mg/g, and the amount of desorption was 2.7.
mg/g, and the readsorption amount was 2.3 mg/g.

特許出願人 日本バイオニクス株式会社代理人 弁理士
 小 堀 貞 文
Patent applicant: Japan Bionics Co., Ltd. Representative Patent attorney: Sadafumi Kobori

Claims (1)

【特許請求の範囲】[Claims] 不純物として二酸化炭素を含有するガスを吸着剤と接触
させて、当該ガスから二酸化炭素を除去する二酸化炭素
の除去方法において、吸着剤として酸化亜鉛、酸化アル
ミニウムおよびアルカリ化合物を混合してなる組成物の
成型体を用いることを特徴とする二酸化炭素の除去方法
In a method for removing carbon dioxide in which a gas containing carbon dioxide as an impurity is brought into contact with an adsorbent to remove carbon dioxide from the gas, a composition comprising a mixture of zinc oxide, aluminum oxide and an alkaline compound as an adsorbent is used. A method for removing carbon dioxide, characterized by using a molded body.
JP63192104A 1988-08-02 1988-08-02 How to remove carbon dioxide Expired - Fee Related JP2651603B2 (en)

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JP63192104A JP2651603B2 (en) 1988-08-02 1988-08-02 How to remove carbon dioxide

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Application Number Priority Date Filing Date Title
JP63192104A JP2651603B2 (en) 1988-08-02 1988-08-02 How to remove carbon dioxide

Publications (2)

Publication Number Publication Date
JPH0243917A true JPH0243917A (en) 1990-02-14
JP2651603B2 JP2651603B2 (en) 1997-09-10

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Cited By (4)

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EP1749571A3 (en) * 2005-07-27 2007-09-05 Air Products and Chemicals, Inc. Co-formed base-treated aluminas for water and CO2 removal
US8178141B2 (en) * 2005-01-27 2012-05-15 The Folger Coffee Company Articles of manufacture and methods for absorbing gasses released by roasted coffee packed in hermetically sealed containers
JP2014083488A (en) * 2012-10-23 2014-05-12 Nippon Steel & Sumitomo Metal Carbon dioxide adsorbent and carbon dioxide recovery apparatus using the same
JP2022190550A (en) * 2021-06-14 2022-12-26 龍祥 權 Carbon dioxide recovery device and carbon dioxide recovery system

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8178141B2 (en) * 2005-01-27 2012-05-15 The Folger Coffee Company Articles of manufacture and methods for absorbing gasses released by roasted coffee packed in hermetically sealed containers
EP1749571A3 (en) * 2005-07-27 2007-09-05 Air Products and Chemicals, Inc. Co-formed base-treated aluminas for water and CO2 removal
US7759288B2 (en) 2005-07-27 2010-07-20 Air Products And Chemicals, Inc. Co-formed base-treated aluminas for water and CO2 removal
JP2014083488A (en) * 2012-10-23 2014-05-12 Nippon Steel & Sumitomo Metal Carbon dioxide adsorbent and carbon dioxide recovery apparatus using the same
JP2022190550A (en) * 2021-06-14 2022-12-26 龍祥 權 Carbon dioxide recovery device and carbon dioxide recovery system

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