JP2003071241A - Acidic gas absorbing material, method for manufacturing the same and gas treatment method - Google Patents

Acidic gas absorbing material, method for manufacturing the same and gas treatment method

Info

Publication number
JP2003071241A
JP2003071241A JP2001264050A JP2001264050A JP2003071241A JP 2003071241 A JP2003071241 A JP 2003071241A JP 2001264050 A JP2001264050 A JP 2001264050A JP 2001264050 A JP2001264050 A JP 2001264050A JP 2003071241 A JP2003071241 A JP 2003071241A
Authority
JP
Japan
Prior art keywords
gas
acidic gas
acidic
absorbent
core particles
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2001264050A
Other languages
Japanese (ja)
Inventor
Tatsuo Kubota
辰男 窪田
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.)
Inax Corp
Original Assignee
Inax Corp
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 Inax Corp filed Critical Inax Corp
Priority to JP2001264050A priority Critical patent/JP2003071241A/en
Publication of JP2003071241A publication Critical patent/JP2003071241A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide an acidic gas absorbing material having high strength and capable of utilizing the greater part of an acidic gas absorbing substance such as slaked lime, or the like, in the absorption of acidic gas, a method for manufacturing the acidic gas absorbing material and a gas treatment method using the acidic gas absorbing material. SOLUTION: The acidic gas absorbing material comprises core particles made of ceramic and an acidic gas absorbing layer covering the surfaces of the core particles. After the surface of the acidic gas absorbing material after the contact with acidic gas is ground, the acidic gas absorbing material is again used in the contact with the acidic gas.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、酸性ガス吸収材、
その製造方法及びこの酸性ガス吸収材を用いたガス処理
方法に関するものである。
TECHNICAL FIELD The present invention relates to an acidic gas absorbent,
The present invention relates to a manufacturing method thereof and a gas treatment method using the acidic gas absorbing material.

【0002】[0002]

【従来の技術】産業廃棄物、都市ゴミ、汚泥等の焼却炉
などから発生する排ガス中の塩化水素、硫黄酸化物、塩
素等の酸性ガスを除去するための処理方法は、湿式法と
乾式法とに大別される。
2. Description of the Related Art Treatment methods for removing acidic gases such as hydrogen chloride, sulfur oxides, chlorine, etc. in exhaust gas generated from incinerators for industrial waste, municipal waste, sludge, etc. are wet method and dry method. Is roughly divided into

【0003】湿式法は充填塔、スプレー塔、棚段塔等の
気液接触装置内で上記有害ガスをアルカリ水溶液又はア
ルカリスラリーと接触させて吸収除去するものである。
この湿式法は、有害成分の除去効率が高い利点はある
が、亜硫酸イオン、硫酸イオン、塩素イオン等のイオン
や重金属の有害成分を含有した廃水が発生し、高度の廃
水処理を要する。更に、処理ガスが高温であるときに
は、排出ガス温度が80℃程度になって水蒸気を多量に
含むため大気中に放出すると白煙となり、拡散が不十分
となるので、再加熱等による白煙防止装置を要するなど
の欠点があった。
In the wet method, the harmful gas is contacted with an aqueous alkali solution or an alkaline slurry in a gas-liquid contactor such as a packed tower, a spray tower or a plate tower to absorb and remove the harmful gas.
Although this wet method has an advantage of high efficiency of removing harmful components, waste water containing ions such as sulfite ions, sulfate ions, and chlorine ions and harmful components of heavy metals is generated, and a high degree of wastewater treatment is required. Furthermore, when the processing gas is at a high temperature, the temperature of the exhaust gas is around 80 ° C and a large amount of water vapor is included, so white smoke is emitted when released into the atmosphere, and diffusion is insufficient, so white smoke is prevented by reheating, etc. There were drawbacks such as the need for equipment.

【0004】一方、乾式法は、水酸化カルシウム、炭酸
カルシウム等のアルカリ性粉末若しくは粒子を吸収材と
し、該吸収材の充填層に排ガスを通して酸性ガスを吸収
させるか、又は排ガス通路に吸収材粉末を噴霧して酸性
ガスと反応させ、然る後捕集する方法である。
On the other hand, in the dry method, alkaline powder or particles such as calcium hydroxide or calcium carbonate is used as an absorbent material, and exhaust gas is absorbed through an exhaust gas through a packed bed of the absorbent material, or absorbent powder is provided in an exhaust gas passage. It is a method of spraying and reacting with acidic gas, and then collecting.

【0005】この乾式法は、高温ガスと固体吸収材との
直接接触反応によるため、廃水の発生はなく、白煙も発
生しない。
Since this dry method is based on the direct contact reaction between the high temperature gas and the solid absorbent, no waste water is generated and no white smoke is generated.

【0006】乾式法のうち、吸収材を充填した層に排ガ
スを通す方式のガス処理方法として、塊状の酸化カルシ
ウム、炭酸カルシウム、若しくは水酸化カルシウム等の
アルカリ物質をペレット状に造粒した酸性ガス吸収材の
充填層を形成し、充填層下部より酸性ガスを吸収した酸
性ガス吸収材を連続的に又は間欠的に抜き出しつつ上方
から酸性ガス吸収材を連続的に又は間欠的に供給して、
充填層中で酸性ガス吸収材を移動させながらガスと接触
させる方法がある。この方法では、充填層から取り出さ
れた酸性ガス吸収材の表面が反応生成物で被覆されてい
て、粒子内部には未反応のアルカリが残存するので、表
面から反応生成物を剥離して分離した後、充填層上部に
戻して再使用している。
Among the dry methods, as a gas treatment method of passing exhaust gas through a layer filled with an absorbent, an acidic gas obtained by pelletizing an alkaline substance such as massive calcium oxide, calcium carbonate, or calcium hydroxide into pellets Forming a packed bed of the absorbent, continuously or intermittently withdrawing the acidic gas absorbent that has absorbed the acidic gas from the lower part of the packed bed, continuously or intermittently supplying the acidic gas absorbent from above,
There is a method in which the acidic gas absorbent is brought into contact with the gas while moving in the packed bed. In this method, the surface of the acidic gas absorbent taken out from the packed bed is covered with the reaction product, and unreacted alkali remains inside the particles, so the reaction product was separated from the surface and separated. After that, it is returned to the upper part of the packed bed for reuse.

【0007】[0007]

【発明が解決しようとする課題】上記従来の酸化カルシ
ウムの造粒体よりなる酸性ガス吸収材は、圧潰強度が低
く、粉化して通気圧損を増大させ易い。また、表面から
反応生成物を剥離して再利用する場合、再使用の度毎に
粒径が小さくなる。粒径が小さくなると、充填層の通気
圧損が増大してガス処理に支障が生じるので、ある程度
粒径が小さくなると、未反応アルカリ物質が残存してい
るにもかかわらず酸性ガス吸収材を廃棄しなければなら
ず、アルカリ物質の無駄が多い。また、廃棄物はアルカ
リ性であるため、廃棄に際して中和処理が必要であり、
新たな処理コストが生じる。
The above-mentioned conventional acidic gas absorbent comprising a granulated body of calcium oxide has a low crushing strength and is easily pulverized to increase the ventilation pressure loss. Further, when the reaction product is peeled from the surface and reused, the particle size becomes smaller each time it is reused. If the particle size becomes small, the ventilation pressure loss of the packed bed will increase, and gas treatment will be hindered.If the particle size becomes small to some extent, the acidic gas absorbent will be discarded despite the unreacted alkaline substance remaining. There is much waste of alkaline substances. In addition, since the waste is alkaline, it requires neutralization before disposal.
New processing costs arise.

【0008】本発明は、このような問題点を解決し、圧
潰強度が高く、また酸性ガス吸収物質(アルカリ物質)
の全て又は大部分を酸性ガス吸収に利用することができ
る酸性ガス吸収材と、その製造方法及びこの酸性ガス吸
収材を用いたガス処理方法を提供することを目的とす
る。
The present invention solves these problems, has a high crushing strength, and is an acidic gas absorbing substance (alkali substance).
It is an object of the present invention to provide an acidic gas absorbent capable of utilizing all or most of the above for absorbing acidic gas, a method for producing the same, and a gas treatment method using the acidic gas absorbent.

【0009】[0009]

【課題を解決するための手段】本発明の酸性ガス吸収材
は、セラミック製の核粒子と、該核粒子の表面を覆う酸
性ガス吸収層とを備えてなるものである。
The acidic gas absorbing material of the present invention comprises ceramic core particles and an acid gas absorbing layer covering the surfaces of the core particles.

【0010】この酸性ガス吸収材は、セラミック製の核
粒子の表面に酸性ガス吸収物質を付着させることにより
製造される。
This acidic gas absorbing material is produced by depositing an acidic gas absorbing substance on the surface of ceramic core particles.

【0011】本発明のガス処理方法は、本発明の核粒子
をガスと接触させて酸性ガスを吸収する方法において、
酸性ガスと接触した後の酸性ガス吸収材の表面を研磨し
た後、該酸性ガス吸収材を再度ガスとの接触に用いるも
のである。
The gas treatment method of the present invention is a method of contacting the core particles of the present invention with a gas to absorb an acidic gas,
After polishing the surface of the acidic gas absorbent after contact with the acidic gas, the acidic gas absorbent is used again for contact with the gas.

【0012】かかる本発明の酸性ガス吸収材は、核粒子
がセラミック製であるため、割れたり潰れたりすること
がなく、粒子強度が高い。
Since the core particles of the acidic gas absorbent of the present invention are made of ceramic, they are not cracked or crushed and have high particle strength.

【0013】この酸性ガス吸収材が酸性ガスと接触する
と、表面から酸性ガス吸収反応が徐々に進行し、酸性ガ
ス吸収速度が小さくなる。そこで、この表面を研磨して
反応生成物を除去すると、酸性ガス吸収材の酸性ガス吸
収速度が回復する。
When the acidic gas absorbing material comes into contact with the acidic gas, the acidic gas absorbing reaction gradually progresses from the surface, and the acidic gas absorbing rate decreases. Therefore, when this surface is polished to remove the reaction product, the acid gas absorption rate of the acid gas absorbent is restored.

【0014】この酸性ガス吸収材は、研磨を繰り返す
と、やがて酸性ガス吸収物質層の全て又は大部分が無く
なるので廃棄する。従って、酸性ガス吸収物質の全部又
は大半を酸性ガス吸収に利用できる。
This acid gas absorbing material is discarded as all or most of the acid gas absorbing material layer is eventually lost after repeated polishing. Therefore, all or most of the acidic gas absorbing substance can be used for absorbing the acidic gas.

【0015】使用し尽した粒子は、セラミック製核粒子
と若干の酸性ガス吸収物質だけであり、最後に残った酸
性ガス吸収物質は殆どすべて酸性ガスと反応して中和さ
れた状態となっているので、別途の中和処理を施すこと
なく廃棄処理できる。また、この核粒子は新たな酸性ガ
ス吸収材の製造に再利用してもよい。
The particles used up were only the ceramic core particles and some acidic gas absorbing substances, and almost all of the acidic gas absorbing substances remaining at the end reacted with the acidic gas to be neutralized. Therefore, it can be disposed of without the need for a separate neutralization treatment. Further, the core particles may be reused for the production of a new acid gas absorbent.

【0016】[0016]

【発明の実施の形態】本発明の酸性ガス吸収材の核粒子
を構成するセラミックとしては、窯業製品の破砕物が好
適であり、例えば、タイルや衛生陶器などの各種陶磁器
製品の破砕物や瓦の破砕物を所定粒度に篩分けしたもの
等が好ましい。核粒子の粒径は1〜6mmとりわけ2〜
5mm程度が好適である。この核粒子は5〜30%程度
の吸水率(24時間吸水率)を有することが好ましい。
吸水率が過度に高いと、核粒子の強度が低く、一方吸水
率が過度に低いと、核粒子の表面に酸性ガス吸収層を付
着させにくくなる。
BEST MODE FOR CARRYING OUT THE INVENTION As the ceramic constituting the core particles of the acidic gas absorbent of the present invention, crushed products of ceramic products are suitable, for example, crushed products and tiles of various ceramic products such as tiles and sanitary ware. Those obtained by sieving the crushed product of 1. The particle size of the core particles is 1 to 6 mm, especially 2 to
About 5 mm is suitable. The core particles preferably have a water absorption rate of about 5 to 30% (24-hour water absorption rate).
If the water absorption is too high, the strength of the core particles is low, while if the water absorption is too low, it becomes difficult to attach the acidic gas absorption layer to the surface of the core particles.

【0017】この核粒子の表面に付着させる酸性ガス吸
収物質としては、生石灰、消石灰、炭酸カルシウム等の
カルシウム系アルカリ物質が好適であるが、吸収能が高
いところから生石灰又は消石灰が好ましい。この酸性ガ
ス吸収物質は、アルカリ物質のみから構成されていても
よく、付着コーティング層の強度を高めるために粘土等
の可塑材成分を少量(例えば10重量%以下程度)含ん
でいてもよい。
As the acidic gas absorbing substance deposited on the surface of the core particles, calcium-based alkaline substances such as quick lime, slaked lime and calcium carbonate are preferable, but quick lime or slaked lime is preferable because of its high absorption capacity. The acidic gas absorbing substance may be composed of only an alkaline substance, and may contain a small amount (for example, about 10% by weight or less) of a plasticizer component such as clay in order to enhance the strength of the adhesion coating layer.

【0018】この酸性ガス吸収物質を核粒子表面に付着
させるには、核粒子に水を吸収させた後、酸性ガス吸収
物質の粉体と混合し、該粉体を核粒子にまぶす如くして
付着させ、次いで乾燥させるのが好ましい。この混合に
際しては、回転式ミキサーや転動造粒機等を用いて、酸
性ガス吸収材を球状に仕上げるのが好ましい。
To attach the acidic gas absorbing substance to the surface of the core particles, water is absorbed by the core particles, and then the powder is mixed with powder of the acidic gas absorbing substance, and the powder is sprinkled on the core particles. It is preferably applied and then dried. At the time of this mixing, it is preferable to finish the acidic gas absorbing material into a spherical shape using a rotary mixer, a rolling granulator or the like.

【0019】なお、消石灰又は炭酸カルシウムの場合
は、そのスラリーと核粒子とを混合することにより核粒
子表面に付着させ、転動させながら乾燥させてコーティ
ング層を核粒子表面に形成してもよい。
In the case of slaked lime or calcium carbonate, the slurry may be mixed with the core particles to be adhered to the surface of the core particles, and the core particles may be dried while rolling to form a coating layer on the surface of the core particles. .

【0020】このようにして酸性ガス吸収物質層を核粒
子表面に形成してなる酸性ガス吸収材の粒径は4〜10
mm程度が好ましい。
The particle size of the acidic gas absorbing material thus obtained by forming the acidic gas absorbing substance layer on the surface of the core particles is 4 to 10
About mm is preferable.

【0021】このようにして製造された酸性ガス吸収材
と被処理ガスとを接触させるには、酸性ガス吸収材の充
填層を形成し、この充填層に被処理ガスを通気すると共
に、充填層の一部から酸性ガス吸収材を取り出し、研磨
処理した後、再び充填層に戻すのが好ましい。特に、充
填層の下部から上向流にて被処理ガスを通気し、充填層
の下部から酸性ガス吸収材を連続的に少量ずつ取り出し
て研磨処理し、充填層の上部に研磨済みの酸性ガス吸収
材を戻すのが好ましい。この場合、研磨処理した酸性ガ
ス吸収材を篩分けして所定粒径以下のものを廃棄し、こ
の廃棄分に見合う量だけ酸性ガス吸収材のニューフィー
ドを供給するのが好ましい。
In order to bring the acid gas absorbent thus produced and the gas to be treated into contact with each other, a packed layer of the acid gas absorbent is formed, and the gas to be treated is aerated through the packed layer. It is preferable that the acidic gas absorbent is taken out from a part of the above, polished, and then returned to the packed bed again. In particular, the gas to be treated is ventilated from the lower part of the packed bed in an upward flow, the acidic gas absorbent is continuously taken out little by little from the lower part of the packed layer, and the polishing treatment is performed. It is preferred to replace the absorbent material. In this case, it is preferable that the acid gas absorbent that has been subjected to the polishing treatment is sieved to discard the particles having a predetermined particle size or less, and a new feed of the acid gas absorbent is supplied in an amount commensurate with the discarded amount.

【0022】[0022]

【実施例】以下に実施例について説明する。EXAMPLES Examples will be described below.

【0023】(1) 酸性ガス吸収材の製造 瓦の不良品を破砕して粒径3〜6mmに篩分けして核粒
子とした。この核粒子100重量部に水50重量部を吸
収させた後、市販の粉末消石灰300重量部と共にパド
ル式ミキサーに投入し、5分間低速撹拌し、次いでミキ
サー内容物を篩を通して消石灰粉末物と造粒物(酸性ガ
ス吸収材)とに分離した。造粒物の平均粒径は8mmで
あった。
(1) Production of Acid Gas Absorbing Material Defective roof tiles were crushed and sieved to a particle size of 3 to 6 mm to obtain core particles. After 50 parts by weight of water was absorbed in 100 parts by weight of the core particles, the mixture was put into a paddle type mixer together with 300 parts by weight of commercially available powdered slaked lime, and the mixture was stirred at a low speed for 5 minutes. Separated into granules (acidic gas absorbent). The average particle size of the granulated product was 8 mm.

【0024】(2) 酸性ガス吸収実験 上記(1)により得た酸性ガス吸収材100gを内径5
0mmのU字形ガラス管に充填した。このガラス管に塩
化水素ガス濃度1000ppmの空気を2.5L/mi
nの割合で通気した。通気当初の流出ガス中の塩化水素
ガス濃度は4ppmであった。
(2) Acid Gas Absorption Experiment 100 g of the acid gas absorbent obtained by the above (1) was used for the inner diameter 5
It was filled in a 0 mm U-shaped glass tube. 2.5 L / mi of air having a hydrogen chloride gas concentration of 1000 ppm was put into this glass tube.
Aeration was performed at a rate of n. The hydrogen chloride gas concentration in the outflow gas at the beginning of aeration was 4 ppm.

【0025】200Hr経過した時点で流出ガス中の塩
化水素ガス濃度が100ppmにまで上昇してきたの
で、通気を中止し、酸性ガス吸収材を取り出し、振動篩
にて表面を研磨した。研磨後の酸性ガス吸収材の平均粒
径は8mmであった。
Since the hydrogen chloride gas concentration in the outflow gas had risen to 100 ppm after 200 hours had passed, ventilation was stopped, the acidic gas absorbent was taken out, and the surface was polished with a vibrating sieve. The average particle size of the acid gas absorbent after polishing was 8 mm.

【0026】この酸性ガス吸収材を再び上記ガラス管に
充填し、同一条件にて塩化水素ガス含有ガスを通気した
ところ、流出ガス中の塩化水素ガス濃度は4ppmであ
った。
When the acidic gas absorbing material was filled in the glass tube again and a hydrogen chloride gas-containing gas was aerated under the same conditions, the hydrogen chloride gas concentration in the outflow gas was 4 ppm.

【0027】180Hr経過した時点で流出ガス中の塩
化水素ガス濃度が100ppmまで上昇してきたので通
気を停止し、再度研磨処理した。研磨後の酸性ガス吸収
材の平均粒径は6mmであった。
At the time when 180 hours passed, the hydrogen chloride gas concentration in the outflow gas had risen to 100 ppm, so ventilation was stopped and polishing was carried out again. The average particle size of the acid gas absorbent after polishing was 6 mm.

【0028】この酸性ガス吸収材を再び上記ガラス管に
充填して同一条件にて通気したところ、流出ガス中の塩
化水素ガス濃度は4ppmであった。150Hr経過後
に流出ガス中の塩化水素ガス濃度が100ppmにまで
上昇してきたので、通気を停止し、酸性ガス吸収材を取
り出した。この酸性ガス吸収材から表面層を剥離して分
析したところ、剥離物中のCaClとCa(OH)
との合計に対するCa(OH)の割合は20モル%で
あった。
When the acidic gas absorbing material was filled in the glass tube again and aerated under the same conditions, the hydrogen chloride gas concentration in the outflow gas was 4 ppm. Since the hydrogen chloride gas concentration in the outflow gas had risen to 100 ppm after the lapse of 150 hours, ventilation was stopped and the acidic gas absorbent was taken out. When the surface layer was peeled from this acidic gas absorbent and analyzed, it was found that CaCl 2 and Ca (OH) 2
The ratio of Ca (OH) 2 to the total of the above was 20 mol%.

【0029】[0029]

【発明の効果】以上の実施例からも明らかな通り、本発
明によると、強度が高いと共に消石灰等の酸性ガス吸収
物質の大部分を酸性ガスの吸収に利用することが可能な
酸性ガス吸収材と、この酸性ガス吸収材の製造方法と、
この酸性ガス吸収材を用いたガス処理方法とが提供され
る。
As is apparent from the above examples, according to the present invention, an acidic gas absorbent having high strength and capable of utilizing most of the acidic gas absorbent such as slaked lime for absorbing acidic gas. And a method of manufacturing this acidic gas absorbent,
A gas treatment method using the acidic gas absorbent is provided.

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 20/04 B01D 53/34 124Z 20/32 ZAB 20/34 Fターム(参考) 4D002 AA02 AA18 AA19 AB01 AC04 BA03 CA07 CA08 DA05 DA12 DA16 EA07 EA13 4G004 BA00 4G066 AA17B AA72C CA23 CA31 DA02 FA01 FA11 GA40 Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) B01J 20/04 B01D 53/34 124Z 20/32 ZAB 20/34 F term (reference) 4D002 AA02 AA18 AA19 AB01 AC04 BA03 CA07 CA08 DA05 DA12 DA16 EA07 EA13 4G004 BA00 4G066 AA17B AA72C CA23 CA31 DA02 FA01 FA11 GA40

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 セラミック製の核粒子と、該核粒子の表
面を覆う酸性ガス吸収層とを備えてなる酸性ガス吸収
材。
1. An acidic gas absorbing material comprising ceramic core particles and an acid gas absorbing layer covering the surfaces of the core particles.
【請求項2】 請求項1において、前記核粒子は窯業製
品の破砕物であることを特徴とする酸性ガス吸収材。
2. The acid gas absorbent according to claim 1, wherein the core particles are crushed products of ceramic products.
【請求項3】 請求項1又は2に記載の酸性ガス吸収材
を製造する方法であって、セラミック製の核粒子の表面
に酸性ガス吸収物質を付着させることを特徴とする酸性
ガス吸収材の製造方法。
3. The method for producing an acidic gas absorbent according to claim 1, wherein the acidic gas absorbent is attached to the surface of ceramic core particles. Production method.
【請求項4】 請求項3において、核粒子に水を吸収さ
せた後、酸性ガス吸収物質の粉体と混合して核粒子の表
面に酸性ガス吸収物質を付着させることを特徴とする酸
性ガス吸収材の製造方法。
4. The acidic gas according to claim 3, wherein after the water is absorbed by the core particles, the core particles are mixed with the powder of the base material for absorbing the acid gas to adhere the base material to the surface of the core particles. Absorbent manufacturing method.
【請求項5】 酸性ガス吸収材と酸性ガスを含む被処理
ガスとを接触させて酸性ガス吸収材に酸性ガスを吸収さ
せるガス処理方法において、 該酸性ガス吸収材は請求項1又は2の方法であり、 酸性ガスと接触した後の酸性ガス吸収材の表面を研磨処
理した後、再度該酸性ガス吸収材を被処理ガスと接触さ
せることを特徴とする酸性ガス吸収材。
5. A gas treatment method in which an acidic gas absorbent and an object gas containing the acidic gas are brought into contact with each other to allow the acidic gas absorbent to absorb the acidic gas, wherein the acidic gas absorbent is the method according to claim 1 or 2. The acid gas absorbing material is characterized in that after polishing the surface of the acid gas absorbing material after contact with the acid gas, the acid gas absorbing material is brought into contact with the gas to be treated again.
JP2001264050A 2001-08-31 2001-08-31 Acidic gas absorbing material, method for manufacturing the same and gas treatment method Pending JP2003071241A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001264050A JP2003071241A (en) 2001-08-31 2001-08-31 Acidic gas absorbing material, method for manufacturing the same and gas treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001264050A JP2003071241A (en) 2001-08-31 2001-08-31 Acidic gas absorbing material, method for manufacturing the same and gas treatment method

Publications (1)

Publication Number Publication Date
JP2003071241A true JP2003071241A (en) 2003-03-11

Family

ID=19090714

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2003071241A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008086866A (en) * 2006-09-29 2008-04-17 Dowa Holdings Co Ltd Treatment method of solid industrial waste
WO2010102371A2 (en) * 2009-03-13 2010-09-16 Universidade Federal De Minas Gerais - Ufmg Ceramic materials for absorbing acid gases, process of preparing same and cyclic acid gas absorption and regeneration process
WO2024004928A1 (en) * 2022-06-27 2024-01-04 日本碍子株式会社 Regeneration method for acid-gas adsorption device, manufacturing method for acid-gas adsorption device, and operating method for acid-gas adsorption device

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008086866A (en) * 2006-09-29 2008-04-17 Dowa Holdings Co Ltd Treatment method of solid industrial waste
WO2010102371A2 (en) * 2009-03-13 2010-09-16 Universidade Federal De Minas Gerais - Ufmg Ceramic materials for absorbing acid gases, process of preparing same and cyclic acid gas absorption and regeneration process
WO2010102371A3 (en) * 2009-03-13 2010-11-11 Universidade Federal De Minas Gerais - Ufmg Ceramic materials for absorbing acid gases, process of preparing same and cyclic acid gas absorption and regeneration process
US8969230B2 (en) 2009-03-13 2015-03-03 Universidade Federal De Minas Gerais Cyclic process for absorption and regeneration of acidic gases
US9724671B2 (en) 2009-03-13 2017-08-08 Universidade Federal De Minas Gerais Ceramic materials for absorption of acidic gases
WO2024004928A1 (en) * 2022-06-27 2024-01-04 日本碍子株式会社 Regeneration method for acid-gas adsorption device, manufacturing method for acid-gas adsorption device, and operating method for acid-gas adsorption device

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