JP2002066255A - Treatment material, treatment element, treatment apparatus, and treatment method of waste gas - Google Patents

Treatment material, treatment element, treatment apparatus, and treatment method of waste gas

Info

Publication number
JP2002066255A
JP2002066255A JP2000254381A JP2000254381A JP2002066255A JP 2002066255 A JP2002066255 A JP 2002066255A JP 2000254381 A JP2000254381 A JP 2000254381A JP 2000254381 A JP2000254381 A JP 2000254381A JP 2002066255 A JP2002066255 A JP 2002066255A
Authority
JP
Japan
Prior art keywords
exhaust gas
adsorbent
ammonia
adsorption
treatment
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.)
Withdrawn
Application number
JP2000254381A
Other languages
Japanese (ja)
Inventor
Kenji Motoyama
健司 本山
Tsutomu Sugiura
勉 杉浦
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.)
Toyobo Co Ltd
Original Assignee
Toyobo Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toyobo Co Ltd filed Critical Toyobo Co Ltd
Priority to JP2000254381A priority Critical patent/JP2002066255A/en
Publication of JP2002066255A publication Critical patent/JP2002066255A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Abstract

PROBLEM TO BE SOLVED: To provide a waste gas treatment method with an extremely high ammonia treatment capability by suppressing the absorption capability of an adsorbent for gases other than ammonia, in a waste gas treatment method for removing an ammonia-containing waste gas by repeating adsorption and desorption steps of removing ammonia in the waste gas by adsorption with the adsorbent and desorbing ammonia after the adsorption. SOLUTION: The ammonia-containing waste gas treatment method comprises the steps of bringing an ammonia-containing waste gas into contact with an adsorbent bearing an acidic substance to adsorb ammonia in the adsorbent and then desorbing ammonia from the adsorbent.

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、排気ガス中の有害
物質等を吸脱着方式にて処理する場合に好適に用いられ
る処理材、処理エレメント及び処理方法に関するもので
あり、詳しくは、例えばアンモニア等の塩基性物質を含
有する排気ガスを吸脱着方式で連続的に処理する場合に
特に好適に用いられる処理材、処理エレメント、処理装
置及び処理方法に関するものである。さらに、耐熱性を
有し、熱に対する安全性の面で排ガス処理に最適に用い
られる処理材に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a treatment material, a treatment element and a treatment method preferably used for treating harmful substances and the like in exhaust gas by an adsorption / desorption method. TECHNICAL FIELD The present invention relates to a processing material, a processing element, a processing apparatus, and a processing method that are particularly preferably used when continuously processing an exhaust gas containing a basic substance such as the above by an adsorption / desorption method. Furthermore, the present invention relates to a treatment material having heat resistance and optimally used for exhaust gas treatment in terms of heat safety.

【0002】[0002]

【従来の技術】有害物質(例えば、悪臭物質)を含有す
る排気ガスの処理方法として、例えば特開昭54−91
66には、吸着材として活性炭を用いて排気ガスを吸脱
着処理する方法が開示されている。このように、従来、
有害物質を吸脱着処理する際、処理材として活性炭を使
用し、排気ガスを吸脱着処理する方法が用いられてき
た。
2. Description of the Related Art As a method of treating exhaust gas containing harmful substances (for example, malodorous substances), Japanese Patent Application Laid-Open No. 54-91 discloses a method.
No. 66 discloses a method of adsorbing and desorbing exhaust gas using activated carbon as an adsorbent. Thus, conventionally,
2. Description of the Related Art When harmful substances are adsorbed and desorbed, a method of using activated carbon as a treatment material and adsorbing and desorbing exhaust gas has been used.

【0003】しかし、活性炭は多種類の悪臭物質に対し
て優れた吸着性能を有するものの、例えばアンモニアの
ように沸点が低く、分子量が小さい塩基性物質に対する
吸着性能が著しく低いため、かような塩基性物質を含有
する排気ガスを処理する場合には、十分な処理性能を得
ることができなかった。
[0003] However, although activated carbon has excellent adsorption performance for various types of malodorous substances, it has a low boiling point, such as ammonia, and remarkably low adsorption performance for basic substances having a low molecular weight. In the case of treating exhaust gas containing a volatile substance, sufficient treatment performance could not be obtained.

【0004】一方で、排気ガス中のアンモニアの吸着性
能を向上させる方法として、例えば、特開昭52−74
589には、活性炭吸着材に硫酸やリン酸等の無機酸や
クエン酸等の有機酸等の酸を添着させた処理剤を用いる
事が開示されている。
On the other hand, as a method for improving the adsorption performance of ammonia in exhaust gas, for example, Japanese Patent Laid-Open Publication No.
No. 589 discloses the use of a treating agent obtained by impregnating an activated carbon adsorbent with an acid such as an inorganic acid such as sulfuric acid or phosphoric acid or an organic acid such as citric acid.

【0005】また、排ガス中のアンモニア等の塩基性ガ
スの吸脱着を連続的に行い処理する方法として、例えば
特開昭52−136895には、無機水素酸のアンモニ
ウム塩や無機酸を添着した微粒状活性炭を用い、流動床
タイプ連続ガス吸着装置にて処理する方法が開示されて
いる。
Further, as a method of continuously absorbing and desorbing a basic gas such as ammonia in exhaust gas and treating the same, for example, Japanese Patent Application Laid-Open No. Sho 52-136895 discloses a method in which an ammonium salt of inorganic hydrogen acid or a fine particle to which inorganic acid is added is disclosed. Discloses a method of treating activated carbon in a fluidized bed type continuous gas adsorption apparatus.

【0006】しかし、上記のように、処理材に強酸を添
着した場合、例えばアンモニア等の塩基性物質の吸着性
能は飛躍的に向上するが、一方で、塩基性物質が強酸と
強くイオン結合し、場合によっては非可逆反応となり、
塩基性物質を吸着した吸着材を、吸着温度以上〜200
℃の高温空気等にて加熱しても、十分に脱着することが
できず、塩基性物質を吸着と脱着を繰り返し行うことで
処理する事ができないと考えられていた。
However, as described above, when a strong acid is added to the treatment material, the performance of adsorbing a basic substance such as ammonia is dramatically improved, but the basic substance is strongly ion-bonded to the strong acid. , In some cases an irreversible reaction,
The adsorbent that has adsorbed the basic substance is placed at a temperature higher than the adsorption temperature to 200
It has been considered that even if heated with high-temperature air at a temperature of, for example, desorption cannot be sufficiently performed, and treatment cannot be carried out by repeatedly adsorbing and desorbing a basic substance.

【0007】また、強酸を使用する為、吸着材の結晶構
造や細孔構造が変化し、塩基性物質以外の例えば有機物
質に対する吸着性能が低下したり、処理材を他の構成材
料と組合せて粒状やシート状やハニカム状(図1)の吸
着素子に加工する場合には、その他の構成材料をも傷め
る為、処理材の脱落が起こったり、加工強度が低下した
り、耐摩耗性が低下し連続使用ができない等の問題を生
じていた。
In addition, since a strong acid is used, the crystal structure and the pore structure of the adsorbent change, the adsorbing performance of, for example, an organic substance other than the basic substance is reduced, or the treatment material is combined with other constituent materials. When processing into a granular, sheet-like, or honeycomb-shaped adsorption element (Fig. 1), other constituent materials are also damaged, so that the processing material falls off, the processing strength decreases, and the wear resistance decreases. However, there has been a problem that continuous use is not possible.

【0008】このように、排気ガス中の塩基性物質を、
吸着材により吸着除去した後、脱着を行い、吸着と脱着
を繰り返し行うことにより、塩基性物質を含有する排気
ガスの処理において、十分な処理性能が得られる処理
材、処理エレメント及び処理装置は得られていないのが
現状である。特に流動床タイプ連続ガス吸着装置に対し
てそのコンパクトさから現在では濃縮装置の主流となっ
ているハニカム式の処理エレメントやハニカム式連続ガ
ス吸着装置は得られていないのが現状である。
Thus, the basic substance in the exhaust gas is
After adsorption and removal by the adsorbent, desorption is performed, and by repeatedly performing adsorption and desorption, in the treatment of exhaust gas containing a basic substance, a processing material, a processing element and a processing apparatus capable of obtaining sufficient processing performance can be obtained. It is not currently done. In particular, at present, a honeycomb-type treatment element and a honeycomb-type continuous gas adsorption device, which are currently the mainstream of concentrators, have not been obtained because of the compactness of the fluidized bed type continuous gas adsorption device.

【0009】[0009]

【発明が解決しようとする課題】本発明は、かかる事情
に着目してなされたものであって、排気ガス中の例えば
アンモニア等の塩基性物質を、吸着材により吸着除去し
た後、脱着を行い、吸着と脱着を繰り返し行うことによ
り、塩基性物質含有排気ガスを処理する排気ガス処理に
おいて、塩基性物質に対する優れた処理性能を有すると
共に塩基性物質以外の例えば有機化合物に対しても優れ
た吸着性能を発現できる処理材、処理エレメント及び処
理方法を提供することを目的とするものである。
SUMMARY OF THE INVENTION The present invention has been made in view of such circumstances, and a method of desorbing and removing a basic substance such as ammonia in exhaust gas by adsorbing and removing the same with an adsorbent. In an exhaust gas treatment for treating a basic substance-containing exhaust gas by repeatedly performing adsorption and desorption, it has excellent processing performance for a basic substance and also excellent adsorption for an organic compound other than the basic substance, for example. It is an object of the present invention to provide a processing material, a processing element, and a processing method that can exhibit performance.

【0010】本発明者は、上記の課題を解決することを
目的に、処理材にて適用する吸着基材の構造、吸着基材
に添着する吸着剤の種類、添着量および脱着方法に関し
て鋭意検討した。
In order to solve the above-mentioned problems, the present inventor has made intensive studies on the structure of the adsorbent substrate applied as a treatment material, the type of adsorbent to be adsorbed on the adsorbent substrate, the amount of the adsorbent, and the desorption method. did.

【0011】その結果、吸着基材に添着する添着剤とし
て、酸性物質を選択し、吸着基材に添着することで、吸
着基材が本来有する吸着性能を維持したまま塩基性物質
に対する優れた吸着性能を発現し、吸着温度以上〜20
0℃の加熱空気による脱着が可能で、吸脱着による連続
使用が可能であることを見出した。
As a result, an acidic substance is selected as an impregnating agent to be impregnated on the adsorbing base material, and by adhering to the adsorbing base material, an excellent adsorbent for a basic substance can be obtained while maintaining the original adsorbing performance of the adsorbing base material. Demonstrates performance and is above the adsorption temperature ~ 20
It has been found that desorption with heated air at 0 ° C. is possible and continuous use by adsorption and desorption is possible.

【0012】さらに、酸性度の低い弱酸より酸性度の高
い強酸を添着剤、例えばリン酸を添着剤として使用する
ことで塩基性物質に対する優れた吸着性能を発現する事
を見出した。
Furthermore, it has been found that by using a strong acid having a higher acidity than that of a weak acid having a low acidity as an impregnating agent, for example, phosphoric acid as an impregnating agent, excellent adsorption performance for a basic substance can be exhibited.

【0013】また、弱酸を使用した場合には吸着した塩
基性物質を吸着温度以上〜200℃の加熱空気による脱
着が十分に可能で、吸脱着による連続使用が可能である
ことを見い出した。さらに、強酸を使用した場合でも、
吸着した塩基性物質と強酸が一部、例えばリン酸を使用
した場合には吸着した塩基性物質の約40%が、強く結
合しているために吸着温度以上〜200℃の加熱空気に
よる脱着が出来ないが、約60%が脱着可能であり、強
酸を使用した場合でも吸脱着による連続使用が可能であ
る事を見出した。
In addition, it has been found that when a weak acid is used, the adsorbed basic substance can be sufficiently desorbed with heated air at a temperature higher than the adsorption temperature to 200 ° C., and can be used continuously by adsorption and desorption. Furthermore, even when using strong acids,
A part of the adsorbed basic substance and the strong acid, for example, when phosphoric acid is used, about 40% of the adsorbed basic substance is strongly bonded, so that desorption by heated air at a temperature higher than the adsorption temperature to 200 ° C is required. Although it was not possible, it was found that about 60% could be desorbed, and even when a strong acid was used, continuous use by adsorption and desorption was possible.

【0014】また、上記吸着基材の種類に関しては、粉
末状活性炭を用いることにより、上記の吸着剤による塩
基性物質に対する吸着性能を最大限に発現し得ると共に
炭化水素類等の有機化合物に対しても優れた吸着性能を
発現し、そして、吸着温度以上〜200℃の加熱空気に
よる脱着も可能であることを見出した。さらに、強酸を
使用した場合には塩基性ガスに対しては優れた吸着性能
を示すが、炭化水素類等の有機化合物に対する吸着性能
低下は弱酸を使用した時よりも大きいことを見出した。
With respect to the type of the above-mentioned adsorbent base material, the use of powdered activated carbon makes it possible to maximize the adsorbing performance of the adsorbent for basic substances and to reduce organic compounds such as hydrocarbons. It has also been found that it exhibits excellent adsorption performance and that desorption with heated air at a temperature higher than the adsorption temperature to 200 ° C. is possible. Furthermore, it has been found that when a strong acid is used, excellent adsorption performance is exhibited for a basic gas, but the decrease in adsorption performance for organic compounds such as hydrocarbons is greater than when a weak acid is used.

【0015】さらに、強酸を使用した場合には処理材を
他の構成材料と組合せて粒状やシート状やハニカム状に
加工する際の強度低下について検討し、ハニカム式連続
ガス吸着装置を適応することで、流動床ではないため耐
摩耗性は必要がないことから、ある程度の強度低下が発
生しても連続処理が可能である事を見出した。さらに、
弱酸に対して強酸であるリン酸等を使用した場合には構
成材料の強度低下がより強くなるが、酸性物質の量や構
成材料の比率・量により強度低下を抑制できることを見
出した。
Further, when a strong acid is used, the reduction in strength when processing the material into a granular, sheet, or honeycomb shape by combining the processing material with another constituent material is examined, and a honeycomb type continuous gas adsorption device is applied. Thus, since it is not a fluidized bed, there is no need for abrasion resistance, and it has been found that continuous processing is possible even if a certain degree of strength reduction occurs. further,
It has been found that when phosphoric acid or the like, which is a strong acid, is used in comparison with a weak acid, the strength of the constituent material is more strongly reduced, but the strength can be suppressed by the amount of the acidic substance and the ratio and the amount of the constituent material.

【0016】さらに、酸性物質の添着量に関しては、一
定の添着量を超えると塩基性物質に対する吸着性能の向
上が見られず、また塩基性物質以外の有機化合物に対す
る吸着性能が低下する事を見出した。
Further, regarding the amount of impregnated acidic substance, it has been found that when the amount impregnated exceeds a certain amount, no improvement in adsorption performance for basic substances is observed, and the adsorption performance for organic compounds other than basic substances is reduced. Was.

【0017】本発明者らは、上記知見を基に、さらに重
ねて検討した結果、本発明を完成するに至ったものであ
る。
The present inventors have conducted further studies based on the above findings, and as a result, have completed the present invention.

【0018】[0018]

【課題を解決するための手段】即ち、本発明は、酸性物
質を粉末状活性炭に添着してなる排気ガスの処理材を提
供するものである。
That is, the present invention provides an exhaust gas treating material obtained by impregnating an acidic substance with powdered activated carbon.

【0019】本発明の排気ガスの処理材の好ましい実施
多様は、前記酸性物質が無機酸および無機酸塩である。
さらに好ましい実施多様は、前記酸性物質がリン酸およ
びリン酸塩化合物である。
In a preferred embodiment of the exhaust gas treating material of the present invention, the acidic substance is an inorganic acid or an inorganic acid salt.
In a further preferred embodiment, the acidic substances are phosphoric acid and phosphate compounds.

【0020】また、本発明は、酸性物質を粉末状活性炭
に添着してなる吸着材をハニカム状構造に成形してなる
排気ガスの処理エレメントを提供するものである。
The present invention also provides an exhaust gas treatment element formed by forming an adsorbent obtained by impregnating an acidic substance into powdered activated carbon into a honeycomb structure.

【0021】さらに、本発明は、塩基性物質を含有する
排気ガスを、酸性物質を粉末状活性炭に添着してなる吸
着材に接触させる工程、該吸着材に塩基性物質を吸着さ
せる工程及び該吸着剤に吸着している塩基性物質を脱着
させる工程を含む排気ガスの処理装置および処理方法を
提供するものである。
Further, the present invention relates to a step of bringing an exhaust gas containing a basic substance into contact with an adsorbent obtained by impregnating an acidic substance with powdered activated carbon, a step of adsorbing the basic substance to the adsorbent, and a step of adsorbing the basic substance. An object of the present invention is to provide an exhaust gas treatment apparatus and a treatment method including a step of desorbing a basic substance adsorbed on an adsorbent.

【0022】さらに、本発明は、塩基性物質を含有する
排気ガスを、酸性物質を粉末状活性炭に添着してなる吸
着材をハニカム構造に成形された処理エレメントに接触
させる工程、該吸着材に塩基性物質を吸着させる工程及
び該吸着剤に吸着している塩基性物質を脱着させる工程
を含む排気ガスの処理装置および処理方法を提供するも
のである。
Further, the present invention provides a step of bringing an exhaust gas containing a basic substance into contact with an adsorbent obtained by impregnating an acidic substance into powdered activated carbon with a treatment element formed into a honeycomb structure. An object of the present invention is to provide an exhaust gas treatment apparatus and a treatment method including a step of adsorbing a basic substance and a step of desorbing the basic substance adsorbed on the adsorbent.

【0023】本発明の前記塩基性物質を脱着させる好ま
しい実施態様は、加熱空気による脱着方式である。
A preferred embodiment of the present invention for desorbing the basic substance is a desorption method using heated air.

【0024】本発明の排気ガスの処理方法の好ましい実
施態様は、前記塩基性ガスがアンモニアである。
In a preferred embodiment of the method for treating exhaust gas according to the present invention, the basic gas is ammonia.

【0025】[0025]

【発明の実施の形態】本発明において、粉末状活性炭に
添着する添着剤は、酸性物質であることが必要である。
酸性物質であるが故に、例えばアンモニア等の塩基性物
質に対して極めて高い吸着性能を発現するからである。
さらに、酸性度の低い弱酸より酸性度の高い強酸を使用
する事で塩基性物質の吸着性能は向上する。
BEST MODE FOR CARRYING OUT THE INVENTION In the present invention, it is necessary that an impregnating agent to be impregnated on powdered activated carbon is an acidic substance.
Because it is an acidic substance, it exhibits extremely high adsorption performance to a basic substance such as ammonia.
Further, by using a strong acid having a higher acidity than a weak acid having a lower acidity, the adsorption performance of a basic substance is improved.

【0026】ここで、酸性物質とは、水溶液とした場合
のpHが7以下になるように種々の酸および金属イオン
と種々の酸を反応させ生成した塩をいい、例えばリン
酸、塩酸、硫酸およびリン酸塩化合物、炭酸塩化合物、
ケイ酸塩化合物、硫酸塩化合物等が挙げられるが、上記
の通り水溶液とした場合に酸性を示す酸性物質であれば
良い。
Here, the acidic substance refers to a salt formed by reacting various acids and metal ions with various acids so that the pH of the aqueous solution becomes 7 or less, such as phosphoric acid, hydrochloric acid, and sulfuric acid. And phosphate compounds, carbonate compounds,
Examples thereof include a silicate compound and a sulfate compound, and any acidic substance that exhibits acidity when used as an aqueous solution as described above may be used.

【0027】上記の酸性物質の中でも、無機酸、中でも
リン酸およびリン酸塩化合物は、難燃剤として用いられ
るように、加熱処理にも安定であり耐熱性が高く、脱着
操作時の加熱による安全性が高く、且つ、吸着基材に対
する接着性が高いので吸着基材への添着が容易であるか
ら好ましい。
Among the above-mentioned acidic substances, inorganic acids, especially phosphoric acid and phosphate compounds, are stable in heat treatment, have high heat resistance, and are safe by heating during desorption, as used as flame retardants. It is preferable because it has a high property and has high adhesiveness to the adsorption substrate, so that it can be easily attached to the adsorption substrate.

【0028】本発明において、吸着剤を添着する吸着基
材は、粉末状活性炭であることが必要である。粉末状活
性炭であれば、例えばアンモニア等の塩基性物質に対す
る吸着剤を粉末状活性炭の多孔質表面に保持することに
より、優れた塩基性物質の吸着性能を発現し得るからで
ある。
In the present invention, the adsorbent substrate to which the adsorbent is attached must be powdered activated carbon. This is because powdery activated carbon can exhibit excellent basic substance adsorption performance by retaining an adsorbent for a basic substance such as ammonia on the porous surface of the powdered activated carbon.

【0029】粉末状活性炭としては、処理する対象であ
る有機化合物に対する吸着性能により適宜選択すればよ
く、特に限定されるものではない。
The powdered activated carbon may be appropriately selected depending on the adsorption performance for the organic compound to be treated, and is not particularly limited.

【0030】粉末状活性炭は、100μm以下の粒径の
ものが好ましい。100μm以上であると、脱落が多く
ハニカム状に形成が困難である。
The powdered activated carbon preferably has a particle size of 100 μm or less. If it is 100 μm or more, it is difficult to form a honeycomb shape due to a large amount of falling off.

【0031】粉末状活性炭は、添着した酸性物質による
塩基性物質に対する吸着性能の発現率が大きく、さらに
疎水性であるため水分の吸着性能が低い事より脱着効率
が良いためより好ましい。具体的には、ヤシガラ炭、セ
ルローズ等の活性炭があるが特に限定されるものではな
い。
Powdered activated carbon is more preferable because it has a high rate of adsorbability of basic substances by the impregnated acidic substance and has a high desorption efficiency because of its low water adsorption performance due to its hydrophobicity. Specifically, activated carbon such as coconut shell charcoal and cellulose is used, but is not particularly limited.

【0032】本発明において、粉末状活性炭に添着する
酸性物質の添着量は、1〜50重量%が好ましく、3〜
40重量%がより好ましく、15〜30重量%が特に好
ましい。添着量が1重量%未満の場合には、塩基ガスに
対する吸着性能が弱く不十分となり、50重量%を越え
る場合には、粉末状活性炭の細孔表面が殆ど添着剤で被
覆され、粉末状活性炭が本来有する有機化合物に対する
吸着性能が十分に発現されないからである。
In the present invention, the amount of the acidic substance to be impregnated on the powdered activated carbon is preferably 1 to 50% by weight, and more preferably 3 to 50% by weight.
It is more preferably 40% by weight, particularly preferably 15 to 30% by weight. When the amount is less than 1% by weight, the adsorption performance for base gas is weak and insufficient. When the amount exceeds 50% by weight, the surface of the pores of the powdered activated carbon is almost covered with the impregnating agent. The reason for this is that the adsorption performance for organic compounds originally possessed is not sufficiently exhibited.

【0033】リン酸を粉末状活性炭に添着させる場合に
は、15〜30重量%程度であれば、塩基性物質及び有
機化合物の両者に対して良好な吸脱着性能を発現し得
る。
When phosphoric acid is impregnated on powdered activated carbon, if it is about 15 to 30% by weight, good adsorption / desorption performance can be exhibited for both basic substances and organic compounds.

【0034】及びリン酸化合物は材料を燃えにくくする
難燃効果を有するため、加熱処理にも安定であり、脱着
操作時の加熱による安全性を高くすることが可能であ
る。
Further, since the phosphoric acid compound has a flame retardant effect of making the material difficult to burn, it is also stable in the heat treatment, and the safety by heating during the desorption operation can be enhanced.

【0035】本発明において、酸性物質を粉末状活性炭
へ添着する方法は、粉末状活性炭の多孔質表面にも酸性
物質を均一に定着できる方法であれば特に限定されるも
のではないが、例えば、リン酸などの酸性物質は、酸性
物質自体がバインダーとして作用するため、リン酸水溶
液中に吸着材を含浸した後に乾燥することで、容易に添
着することが可能である。
In the present invention, the method of attaching the acidic substance to the powdered activated carbon is not particularly limited as long as the acidic substance can be uniformly fixed on the porous surface of the powdered activated carbon. Acidic substances such as phosphoric acid can be easily attached by impregnating the adsorbent in an aqueous phosphoric acid solution and then drying, since the acidic substance itself acts as a binder.

【0036】本発明の排気ガスの処理エレメントは、上
記で説明した処理材を造粒したものを充填した吸着素
子、吸着材をハニカム状構造に成形した吸着素子などが
好適に用いられるが、中でも、ハニカム状構造に成形し
た吸着素子は工業的に利用する際の利便性が高く好まし
い。
As the exhaust gas treatment element of the present invention, an adsorption element filled with a granulation of the above-described treatment material, an adsorption element formed by molding the adsorbent into a honeycomb structure, and the like are preferably used. On the other hand, an adsorption element formed into a honeycomb-like structure is preferable because it is convenient for industrial use.

【0037】本発明の排気ガスの処理装置及び処理方法
は、塩基性物質、好ましくはアンモニアを含有する排気
ガスを、酸性物質を粉末状活性炭に添着してなる吸着材
に接触させる工程、該吸着材に塩基性物質を吸着させる
工程及び該吸着剤に吸着している塩基性物質を脱着させ
る工程を含むことが必要である。吸着材を長期間使用
し、アンモニア含有排気ガスを処理するためである。
The exhaust gas treatment apparatus and method according to the present invention include a step of contacting an exhaust gas containing a basic substance, preferably ammonia, with an adsorbent obtained by impregnating an acidic substance with powdered activated carbon. It is necessary to include a step of adsorbing a basic substance on a material and a step of desorbing the basic substance adsorbed on the adsorbent. This is because the adsorbent is used for a long time to process the ammonia-containing exhaust gas.

【0038】本発明のアンモニア含有排気ガスの処理方
法にて処理されるアンモニアを含有する排気ガスは、ア
ンモニア単体ガスは基より、アンモニアと他の有機溶剤
等の悪臭物質を含む混合ガスの場合でも、本発明を適応
する事ができる。
The ammonia-containing exhaust gas to be treated by the method for treating ammonia-containing exhaust gas of the present invention may be a mixed gas containing ammonia and other malodorous substances such as other organic solvents rather than a simple ammonia gas. The present invention can be applied.

【0039】具体的には、酸性物質を添着した吸着材
が、ハニカム状構造に成形された吸着素子を吸着ゾーン
と脱着ゾーンにわけて、吸着ゾーンに排気ガスを通気
し、排気ガス中のアンモニアを吸着除去する操作と、一
方で、脱着ゾーンに少量の加熱空気を通気し、吸着され
たアンモニアを脱着する操作を連続的に繰り返してアン
モニアを除去する排気ガス処理装置及び処理方法(図
2)があるが、アンモニアを含有する排気ガスを、酸性
物質を添着した吸着材に接触させ、該吸着材にアンモニ
アを吸着させた後に脱着させる工程を含む排気ガス処理
方法であれば良く、特にこれらに限定されるものではな
い。また、脱着されたアンモニアは、例えば、燃焼装置
により酸化分解処理し清浄空気とする。
Specifically, an adsorbent to which an acidic substance is attached divides an adsorption element formed into a honeycomb structure into an adsorption zone and a desorption zone, and vents exhaust gas into the adsorption zone to remove ammonia contained in the exhaust gas. Exhaust gas treatment apparatus and method for removing ammonia by continuously repeating the operation of adsorbing and removing ammonia and the operation of desorbing the adsorbed ammonia by continuously passing a small amount of heated air through the desorption zone (FIG. 2) However, any method may be used as long as it is an exhaust gas treatment method including a step of contacting an exhaust gas containing ammonia with an adsorbent to which an acidic substance is attached, and desorbing the ammonia after adsorbing the ammonia on the adsorbent. It is not limited. The desorbed ammonia is oxidized and decomposed by a combustion device to produce clean air.

【0040】本発明におけるアンモニア含有排気ガスの
処理方法の諸特性の測定方法は次の通りである。
The method for measuring various characteristics of the method for treating ammonia-containing exhaust gas in the present invention is as follows.

【0041】アンモニアおよびトルエンの吸着性能
(吸着率q及びQ)の測定(JIS−K−1474に準
ずる) 吸着試験用U字管に吸着素子を入れ温度25℃±0.5
℃に調合した溶剤蒸気吸着性能試験装置(図3)に50
0ppmのアンモニア混合空気および3000ppmの
トルエン混合空気を流し60分間吸着させ、吸着素子の
重量増加を測定する。吸着率q及びQは次式で求める。 q及びQ(g/l)=P/S×100 ここで Pは吸着素子の増量(g) Sは吸着素子の体積(l) 実施例、比較例で示す活性炭素材吸着素子のトルエンの
ブランクの吸着率は 、活性炭素材吸着素子 Q=25.0(体積%) 処理性能(除去率)の測定 排気ガス処理装置(図2)を用い処理性能(η)の測定
を行う。除去率は次式にて求める。 η(%)=(I−O)/I×100 ここで Iは処理ガス入口濃度(ppm) Oは処理ガス出口濃度(ppm) Iの処理ガス入口濃度およびOの処理ガス出口濃度の測
定は、装置運転開始から1時間毎に、吸着と脱着操作が
十分に繰り返され処理ガス出口濃度が一定の濃度を示し
変化しなくなる、すなわち処理ガス出口濃度が安定する
まで行う。表1に示すアンモニア処理性能は、処理ガス
出口濃度が安定した際に測定された処理ガス入口濃度お
よび処理ガス出口濃度測定値より計算する。 流動性および耐摩耗性の測定 流動性:流動性評価装置(図4)を用いて流動性の評価
を行う。5.6mmφの口径にて微粒状活性炭が流れる
か否かを測定した。微粒状活性炭と添着材を添着した微
粒状活性炭と比較を行い流動性を判断した。 耐摩耗性:添着材を添着した微粒状活性炭を三角フラス
コに入れ一定の強さで一定時間攪拌した。その後の微粒
状活性炭の破砕状況を目視にて判断した。 難燃性の測定 サンプル管に吸着素子を入れて恒温層に設置し、吸着素
子に4.0m/sの空気を供給しつつ、恒温層温度を5
℃/minで昇温させる。その際の吸着素子の温度及び
発生CO濃度を測定し、難燃性を判断する。
Measurement of adsorption performance (adsorption rate q and Q) of ammonia and toluene (according to JIS-K-1474) Place the adsorption element in a U-shaped tube for adsorption test, temperature 25 ° C. ± 0.5
50 ° C in the solvent vapor adsorption performance tester (Fig. 3)
A mixture of 0 ppm ammonia mixed air and 3000 ppm toluene mixed air is allowed to flow for adsorption for 60 minutes, and the weight increase of the adsorption element is measured. The adsorption rates q and Q are determined by the following equations. q and Q (g / l) = P / S × 100 where P is the increase in the amount of the adsorption element (g) S is the volume of the adsorption element (l) The toluene blank of the activated carbon material adsorption element shown in Examples and Comparative Examples The adsorption rate was determined by the activated carbon material adsorption element Q = 25.0 (vol%) Measurement of treatment performance (removal rate) The treatment performance (η) was measured using an exhaust gas treatment device (FIG. 2). The removal rate is calculated by the following equation. η (%) = (I−O) / I × 100 where I is the processing gas inlet concentration (ppm) O is the processing gas outlet concentration (ppm) The measurement of the I processing gas inlet concentration and the O processing gas outlet concentration is At every hour from the start of the operation of the apparatus, the adsorption and desorption operations are sufficiently repeated until the processing gas outlet concentration shows a constant concentration and does not change, that is, until the processing gas outlet concentration is stabilized. The ammonia processing performance shown in Table 1 is calculated from the measured values of the processing gas inlet concentration and the processing gas outlet concentration measured when the processing gas outlet concentration is stabilized. Measurement of fluidity and wear resistance Fluidity: The fluidity is evaluated using a fluidity evaluation device (FIG. 4). It was measured whether fine-grained activated carbon flows at a diameter of 5.6 mmφ. Fluidity was determined by comparing the fine granular activated carbon with the fine granular activated carbon impregnated with the impregnating material. Abrasion resistance: The fine-grained activated carbon to which the impregnating material was impregnated was placed in an Erlenmeyer flask and stirred at a constant strength for a constant time. The subsequent crushing of the fine granular activated carbon was visually determined. Measurement of flame retardancy The adsorption element was placed in a sample tube and placed in a thermostat, and the temperature of the thermostat was adjusted to 5 while supplying 4.0 m / s of air to the adsorption element.
The temperature is raised at ° C / min. At that time, the temperature of the adsorption element and the generated CO concentration are measured to determine the flame retardancy.

【0042】[0042]

【実施例】以下の実施例および比較例に基づいて本発明
のアンモニア含有排気ガスの処理方法について説明す
る。 (実施例1)吸着材として粉末状活性炭を60重量%
と、他の構成材料としてケブラー、ガラス、PVA、ポ
リ酢酸ビニルエマルジョンを40重量%で構成される波
長3.1mm、波高2.1mmのハニカム状構造の吸着
素子を、30重量%のリン酸水溶液に含浸し、100℃
で乾燥させ、リン酸を30重量%添着した粉末状活性炭
を使用したハニカム状吸着素子を得た。このハニカム状
吸着素子のアンモニア吸着性能およびアンモニアの以外
の悪臭成分であるトルエン吸着性能を測定した。リン酸
を使用している事で、アンモニアの吸着性能は飛躍的に
向上し、トルエン吸着性能の低下も少ない良好な結果を
得た(表1)。次にこのハニカム状吸着素子を排気ガス
処理装置(図2)に適応して、素子を吸着ゾーンと脱着
ゾーンに分けて、吸着ゾーンにアンモニア100ppm
の排気ガスを通気してアンモニアを吸着除去する操作
と、一方で、脱着ゾーンに、吸着ゾーンに通気する風量
に対して、1/20の風量の130℃の加熱空気を通気
し、アンモニアを脱着する操作を連続的に行いアンモニ
アの処理性能を測定した。リン酸を添着した粉末状活性
炭吸着材を用いる事で、アンモニアの脱着が可能で、ア
ンモニア処理性能が飛躍的に向上する良好な結果を得た
(表1)。また、難燃性の測定を行った。ハニカム状吸
着素子の急な昇温は見られず、測定後の吸着素子は強度
が保たれていた。
EXAMPLES The method for treating ammonia-containing exhaust gas of the present invention will be described based on the following examples and comparative examples. (Example 1) 60% by weight of powdered activated carbon as an adsorbent
And an adsorbing element having a honeycomb-like structure having a wavelength of 3.1 mm and a wave height of 2.1 mm composed of 40% by weight of Kevlar, glass, PVA, and polyvinyl acetate emulsion as other constituent materials, and a phosphoric acid aqueous solution of 30% by weight. Impregnated at 100 ° C
To obtain a honeycomb-shaped adsorption element using powdered activated carbon impregnated with 30% by weight of phosphoric acid. The ammonia adsorption performance of this honeycomb-shaped adsorption element and the adsorption performance of toluene, which is a malodorous component other than ammonia, were measured. By using phosphoric acid, the ammonia adsorption performance was dramatically improved, and good results were obtained with little decrease in toluene adsorption performance (Table 1). Next, this honeycomb-shaped adsorption element is adapted to an exhaust gas treatment device (FIG. 2), and the element is divided into an adsorption zone and a desorption zone.
The operation of adsorbing and removing ammonia by passing the exhaust gas through, and on the other hand, passing 130 ° C. of heated air at 1/20 of the air flow to the desorption zone with respect to the air flow to the adsorption zone to desorb ammonia This operation was continuously performed, and the treatment performance of ammonia was measured. By using the powdered activated carbon adsorbent to which phosphoric acid was impregnated, ammonia could be desorbed, and good results were obtained in which the ammonia treatment performance was dramatically improved (Table 1). In addition, the flame retardancy was measured. No sudden rise in temperature of the honeycomb-shaped adsorption element was observed, and the adsorption element after the measurement maintained its strength.

【0043】(比較例1)吸着材として粉末状活性炭を
60重量%と、他の構成材料としてケブラー、ガラス、
PVA、ポリ酢酸ビニルエマルジョンを40重量%で構
成される波長3.1mm、波高2.1mmのハニカム状
構造の吸着素子を作成した。このハニカム状吸着素子の
アンモニア吸着性能を測定した。アンモニアの吸着性能
は実施例に比べ著しく低い結果となった。次に、このハ
ニカム状吸着素子を排気ガス処理装置(図2)に適応し
て、素子を吸着ゾーンと脱着ゾーンに分けて、吸着ゾー
ンにアンモニア100ppmの排気ガスを通気してアン
モニアを吸着除去する操作と、一方で、脱着ゾーンに、
吸着ゾーンに通気する風量に対して、1/20の風量の
130℃の加熱空気を通気し、アンモニアを脱着する操
作を連続的に行いアンモニアの処理性能を測定した。ア
ンモニアの脱着が可能であるが、実施例に比べ、アンモ
ニア処理性能が著しく低い結果を得た(表1)。また、
難燃性の測定を行った。ハニカム状吸着素子の急な昇温
が見られ、測定後の吸着素子は白く灰化し強度が保たれ
ておらず、燃焼していた。
Comparative Example 1 60% by weight of powdered activated carbon was used as an adsorbent, and Kevlar, glass,
An adsorbing element having a honeycomb structure having a wavelength of 3.1 mm and a wave height of 2.1 mm, comprising PVA and polyvinyl acetate emulsion at 40% by weight, was prepared. The ammonia adsorption performance of this honeycomb-shaped adsorption element was measured. The ammonia adsorption performance was significantly lower than that of the example. Next, this honeycomb-shaped adsorbing element is adapted to an exhaust gas treatment apparatus (FIG. 2), the element is divided into an adsorption zone and a desorption zone, and 100 ppm ammonia gas is passed through the adsorption zone to adsorb and remove ammonia. Operation and, on the other hand, in the desorption zone,
Heating air at 130 ° C. was blown at 1/20 of the air flow to the adsorption zone, and the operation for desorbing ammonia was continuously performed to measure the ammonia treatment performance. Although desorption of ammonia was possible, the result that the ammonia treatment performance was significantly lower than that of the example was obtained (Table 1). Also,
The flame retardancy was measured. A sudden rise in the temperature of the honeycomb-shaped adsorption element was observed, and the adsorption element after measurement was incinerated white and the strength was not maintained, and the element was burning.

【0044】(比較例2)吸着材を用いずに、他の構成
材料としてケブラー、ガラス、PVA、ポリ酢酸ビニル
エマルジョンで構成される波長3.1mm、波高2.1
mmのハニカム状構造の吸着素子を、30重量%のリン
酸水溶液に含浸し、100℃で1時間乾燥させ、リン酸
を30重量%添着したハニカム状吸着素子を得た。この
ハニカム状素子のアンモニア吸着性能を測定した。リン
酸を含有しているために、アンモニアを吸着するが実施
例に対して著しく吸着性能が低い結果を得た(表1)。
このことから、アンモニアの添着剤による吸着には、吸
着材の特徴である多孔性が影響していると考えられる。
(Comparative Example 2) A wavelength of 3.1 mm, a wave height of 2.1 composed of Kevlar, glass, PVA, and polyvinyl acetate emulsion as other constituent materials without using an adsorbent.
The adsorbing element having a honeycomb structure having a thickness of 3 mm was impregnated with a 30% by weight aqueous phosphoric acid solution and dried at 100 ° C. for 1 hour to obtain a honeycomb-shaped adsorbing element to which 30% by weight of phosphoric acid was impregnated. The ammonia adsorption performance of this honeycomb element was measured. Since the phosphoric acid was contained, ammonia was adsorbed, but the results were significantly lower than those of Examples (Table 1).
From this, it is considered that the adsorption of the ammonia by the adsorbent is affected by the porosity which is a characteristic of the adsorbent.

【0045】(比較例3)粉末状活性炭を30重量%の
リン酸水溶液に含浸し、100℃で1時間乾燥させ、リ
ン酸を30重量%添着した粉末状活性炭を得た。これの
流動性及び耐摩耗性にいて測定した。活性炭の粉化が有
り、また流動性は悪かった。やはりリン酸等の強酸を使
用した場合には流動層タイプによる連続処理は流動性の
低下および耐摩耗性の低下からハニカム方式による連続
処理に対して優位性が低いと考えられる。(表1)
Comparative Example 3 Powdered activated carbon was impregnated with a 30% by weight aqueous phosphoric acid solution and dried at 100 ° C. for 1 hour to obtain a powdered activated carbon impregnated with 30% by weight of phosphoric acid. The fluidity and abrasion resistance were measured. Activated carbon was powdered and fluidity was poor. Also, when a strong acid such as phosphoric acid is used, continuous treatment with a fluidized bed type is considered to be less advantageous than continuous treatment with a honeycomb system due to a decrease in fluidity and abrasion resistance. (Table 1)

【0046】[0046]

【表1】 [Table 1]

【0047】[0047]

【発明の効果】以上、説明した様に本発明のアンモニア
含有排気ガスの処理方法は、アンモニアを含有する排気
ガスを、無機酸を添着した吸着材に接触させ、該吸着材
にアンモニアを吸着させた後に脱着させる工程を含む
事、特に該無機酸にリン酸を使用する事と、該吸着材に
粉末状活性お炭を使用する事で、吸着材のアンモニア以
外の吸着性能を低下させず、また、シート状やハニカム
状に加工する際の他の構成材料を痛めることなく加工で
き、そして、その吸着材を用いる事で、アンモニアの吸
着・脱着処理可能として、アンモニアの処理性能を極め
て高くする事を可能とする効果を有する。
As described above, in the method for treating ammonia-containing exhaust gas according to the present invention, the ammonia-containing exhaust gas is brought into contact with an adsorbent to which an inorganic acid is attached, and the ammonia is adsorbed on the adsorbent. Including the step of desorption after, especially using phosphoric acid as the inorganic acid, by using powdered activated carbon as the adsorbent, without lowering the adsorption performance of the adsorbent other than ammonia, In addition, processing can be performed without damaging other constituent materials when processing into a sheet shape or a honeycomb shape, and by using the adsorbent, ammonia can be adsorbed and desorbed, thereby greatly improving the processing performance of ammonia. It has the effect of making things possible.

【図面の簡単な説明】[Brief description of the drawings]

【図1】 図は本発明の耐熱性吸着素子の形状であるハ
ニカム状の形状を示す。
FIG. 1 shows a honeycomb shape which is a shape of a heat resistant adsorption element of the present invention.

【図2】 図2はハニカム状吸着素子を使用し、素子を
吸着ゾーンと脱着ゾーンにわけて、吸・脱着操作を繰り
返し連続的に有機溶剤を除去する排気ガス処理方法を示
す。
FIG. 2 shows an exhaust gas treatment method that uses a honeycomb-shaped adsorption element, divides the element into an adsorption zone and a desorption zone, and repeats adsorption and desorption operations to continuously remove an organic solvent.

【図3】 図3は吸着材の吸着性能を評価する装置を示
す。
FIG. 3 shows an apparatus for evaluating the adsorption performance of an adsorbent.

【図4】 図4は吸着材の流動性を評価する装置を示
す。
FIG. 4 shows an apparatus for evaluating the fluidity of an adsorbent.

【符号の説明】[Explanation of symbols]

A1、A2 温度調節用蛇管 B1、B2、B3 共通すり合わせ濾過板付ガス洗浄
瓶(250ml) C 混合瓶(球内径60mm二球連続式) D 吸着試験用U字管 E 三方コック F1 溶剤蒸気発生空気流量計 F2 希釈空気用流量計 N 恒温槽又は恒温水槽 H 余剰ガス出口 I 乾燥空気入口 J 排気口 K1,K2 ガス流量調節コック L 溶剤 2a フルート部 2b ライナー部
A1, A2 Serpentine tube for temperature control B1, B2, B3 Gas washing bottle with common ground filter plate (250 ml) C Mixing bottle (sphere inner diameter 60 mm two-ball continuous type) D U-tube for adsorption test E Three-way cock F1 Solvent vapor generated air flow F2 Flow meter for dilution air N Constant temperature bath or constant temperature water bath H Excess gas outlet I Dry air inlet J Exhaust port K1, K2 Gas flow control cock L Solvent 2a Flute portion 2b Liner portion

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D002 AA13 AB01 BA03 BA12 CA05 DA26 EA08 4G066 AA05C AA50B AA71D AC12D AC26D AE01B BA07 BA36 CA08 CA29 DA02 FA12 FA25 FA28 GA01 GA06 GA16  ──────────────────────────────────────────────────続 き Continued on the front page F term (reference) 4D002 AA13 AB01 BA03 BA12 CA05 DA26 EA08 4G066 AA05C AA50B AA71D AC12D AC26D AE01B BA07 BA36 CA08 CA29 DA02 FA12 FA25 FA28 GA01 GA06 GA16

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 酸性物質を粉末状活性炭に添着してなる
ことを特徴とする難燃性排気ガスの処理材。
1. A flame-retardant exhaust gas treatment material comprising an acidic substance impregnated in powdered activated carbon.
【請求項2】 前記酸性物質が、無機酸および無機酸塩
であることを特徴とする請求項1に記載の排気ガスの処
理材。
2. The exhaust gas treating material according to claim 1, wherein the acidic substance is an inorganic acid or an inorganic acid salt.
【請求項3】 前記酸性物質が、リン酸塩化合物である
ことを特徴とする請求項1ないし2に記載の排気ガスの
処理材。
3. The exhaust gas treating material according to claim 1, wherein the acidic substance is a phosphate compound.
【請求項4】 前記酸性物質が、リン酸であることを特
徴とする請求項1乃至3のいずれかに記載の排気ガスの
処理材。
4. The exhaust gas treating material according to claim 1, wherein the acidic substance is phosphoric acid.
【請求項5】 酸性物質を粉末状活性炭に添着してなる
吸着材をハニカム状構造に成形してなることを特徴とす
る請求項1乃至4のいずれかに記載の排気ガスの処理エ
レメント。
5. The exhaust gas treatment element according to claim 1, wherein the adsorbent obtained by impregnating the acidic substance with the powdered activated carbon is formed into a honeycomb structure.
【請求項6】 塩基性物質を含有する排気ガスを、酸性
物質を粉末状活性炭に添着してなる吸着材に接触させる
工程、該吸着材に塩基性物質を吸着させる工程及び該吸
着剤に吸着している塩基性物質を脱着させる工程を含む
ことを特徴とする請求項1乃至5のいずれかに記載の排
気ガスの処理装置及び処理方法。
6. A step of bringing an exhaust gas containing a basic substance into contact with an adsorbent obtained by attaching an acidic substance to powdered activated carbon, a step of causing the adsorbent to adsorb a basic substance, and an step of adsorbing the adsorbent. The exhaust gas processing apparatus and method according to any one of claims 1 to 5, further comprising a step of desorbing the basic substance.
【請求項7】 塩基性物質を含有する排気ガスを、酸性
物質を粉末状活性炭に添着してなる吸着材をハニカム構
造に成形された処理エレメントに接触させる工程、該吸
着材に塩基性物質を吸着させる工程及び該吸着剤に吸着
している塩基性物質を脱着させる工程を含むことを特徴
とする請求項1乃至6のいずれかに記載の排気ガスの処
理装置及び処理方法。
7. A step of bringing an exhaust gas containing a basic substance into contact with an adsorbent obtained by impregnating an acidic substance to powdered activated carbon with a treatment element formed in a honeycomb structure, wherein the basic substance is added to the adsorbent. The exhaust gas treatment apparatus and method according to any one of claims 1 to 6, comprising a step of adsorbing and a step of desorbing a basic substance adsorbed on the adsorbent.
【請求項8】 前記塩基性物質を脱着させる工程が加熱
空気による脱着方式であることを特徴とする請求項6乃
至7のいずれかに記載の排気ガスの処理装置及び処理方
法。
8. The exhaust gas processing apparatus and method according to claim 6, wherein the step of desorbing the basic substance is a desorption method using heated air.
【請求項9】 前記塩基性ガスがアンモニアであること
を特徴とする請求項7乃至8のいずれかに記載の排気ガ
スの処理方法。
9. The exhaust gas treatment method according to claim 7, wherein the basic gas is ammonia.
JP2000254381A 2000-08-24 2000-08-24 Treatment material, treatment element, treatment apparatus, and treatment method of waste gas Withdrawn JP2002066255A (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005177674A (en) * 2003-12-22 2005-07-07 Toyobo Co Ltd Basic gas treatment system
JP2012249742A (en) * 2011-06-01 2012-12-20 Suminoe Textile Co Ltd Flame retardant deodorizing filter and method of manufacturing the same
JP2014050416A (en) * 2012-09-04 2014-03-20 Suminoe Textile Co Ltd Flame-retardant deodorant filter
EP3318313A3 (en) * 2016-11-08 2018-06-20 Hamilton Sundstrand Corporation Sorbent systems and methods
CN111330436A (en) * 2020-03-13 2020-06-26 上海梅思泰克环境股份有限公司 Preparation method and device of deodorizing filter material

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005177674A (en) * 2003-12-22 2005-07-07 Toyobo Co Ltd Basic gas treatment system
JP2012249742A (en) * 2011-06-01 2012-12-20 Suminoe Textile Co Ltd Flame retardant deodorizing filter and method of manufacturing the same
JP2014050416A (en) * 2012-09-04 2014-03-20 Suminoe Textile Co Ltd Flame-retardant deodorant filter
EP3318313A3 (en) * 2016-11-08 2018-06-20 Hamilton Sundstrand Corporation Sorbent systems and methods
US10391469B2 (en) 2016-11-08 2019-08-27 Hamilton Sundstrand Corporation Sorbent systems and methods
CN111330436A (en) * 2020-03-13 2020-06-26 上海梅思泰克环境股份有限公司 Preparation method and device of deodorizing filter material

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