JP2002045690A - Treatment material, treatment element, treatment equipment and treatment process for exhaust gas - Google Patents

Treatment material, treatment element, treatment equipment and treatment process for exhaust gas

Info

Publication number
JP2002045690A
JP2002045690A JP2000240205A JP2000240205A JP2002045690A JP 2002045690 A JP2002045690 A JP 2002045690A JP 2000240205 A JP2000240205 A JP 2000240205A JP 2000240205 A JP2000240205 A JP 2000240205A JP 2002045690 A JP2002045690 A JP 2002045690A
Authority
JP
Japan
Prior art keywords
exhaust gas
ammonia
adsorption
treatment
adsorbent
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Withdrawn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
JP2000240205A
Other languages
Japanese (ja)
Inventor
Kenji Motoyama
健志 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 JP2000240205A priority Critical patent/JP2002045690A/en
Publication of JP2002045690A publication Critical patent/JP2002045690A/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Withdrawn legal-status Critical Current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 an exhaust gas treatment process which comprises adsorbing and removing ammonia in an exhaust gas with an adsorbing material, thereafter desorbing the adsorbed ammonia from the adsorbing material and repeatedly performing such adsorption/desorption of ammonia to remove ammonia from the ammonia-containing exhaust gas, and enables inhibition of reduction in performance with respect to adsorption of gases other than ammonia of the adsorbing material and remarkable enhancement of ammonia treatment performance of the adsorbing material. SOLUTION: This exhaust gas treatment process involves a stage for bringing an ammonia-containing exhaust gas into contact with a honeycomb-shaped adsorbing material obtained by impregnating an acidic substance to a honeycomb-shaped base material of the adsorbing material, to adsorb ammonia on the adsorbing material, and thereafter desorbing the adsorbed ammonia from the adsorbing material.

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、処理装置及び処理方法に関
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。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a processing material, a processing element, a processing apparatus and a processing method which are preferably used when processing harmful substances and the like in exhaust gas by an adsorption / desorption method. For example, 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 ammonia by an adsorption / desorption method.

【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 such a low boiling point as ammonia, for example, that it has an extremely low adsorption performance for basic substances having a small molecular weight. When treating an exhaust gas containing a basic 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 treatment 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
スを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。
As a method for continuously absorbing and desorbing a basic gas such as ammonia in exhaust gas, Japanese Unexamined Patent Publication (Kokai) No. 52-136895 discloses a method for treating fine particles containing an ammonium salt of an inorganic hydrogen acid or an inorganic acid. 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、処理材にリン酸等
の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。
[0006] However, as described above, when a strong acid such as phosphoric acid is added to the treatment material, the performance of adsorbing a basic substance such as ammonia is dramatically improved. Strongly ionically bonded, and in some cases, becomes an irreversible reaction, and the adsorbent that has adsorbed the basic substance cannot be sufficiently desorbed even when heated with high-temperature air at a temperature higher than the adsorption temperature to 200 ° C. It was thought that the treatment could not be performed by repeatedly performing adsorption and desorption of the toxic 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
料と組み合わ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
痛める為、処理剤の脱落が起こったり、加工物の強度が
低下したり、耐摩耗性が低下し、連続使用が出来ない等
の問題を生じていた。
In addition, since a strong acid is used, the crystal structure and pore structure of the adsorbent change, the adsorbability of organic substances other than basic substances, for example, decreases, or the treatment material is combined with other constituent materials. Granular, sheet and honeycomb shapes (Fig. 1)
When processing into an adsorption element, the processing agent may fall off, the strength of the processed material may be reduced, the wear resistance may be reduced, and continuous use may not be possible. Had a problem.

【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、処理
装置および処理方法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, a processing apparatus, 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、また、ハニカム状
構造とした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 adhered to the adsorbing substrate, and the acidic substance is impregnated on the adsorbing substrate, so that the excellent adsorbing property for the basic substance can be maintained while maintaining the original adsorption performance of the adsorbing substrate. Demonstrates performance and is above the adsorption temperature ~ 20
It has been found that desorption with hot air at 0 ° C. is possible and continuous use by adsorption and desorption with a honeycomb structure 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。
Further, 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. Further, even when a strong acid is used, 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 the adsorption temperature is higher than the adsorption temperature. Desorption by heated air at ~ 200 ° C is not possible, but about 60% is desorbable, and it has been found that continuous use by adsorption and desorption is possible even when a strong acid is used.

【0014】また、上記吸着基材の種類に関しては、多
孔性吸着基材、特に、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、さらに、吸着温度以上〜20
0℃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。
[0014] Regarding the type of the above-mentioned adsorbent substrate, the use of a porous adsorbent substrate, particularly activated carbon, makes it possible to maximize the adsorbing performance of the adsorbent for basic substances and to use hydrocarbons. Etc., which exhibit excellent adsorption performance to organic compounds such as
It has been found that desorption with heated air at 0 ° C. is also possible. Furthermore, it has been found that when a strong acid is used, the basic gas exhibits excellent adsorption performance, but the performance decrease for organic compounds such as hydrocarbons is larger 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
他の構成材料と組み合わ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事で、流動床では無いため
に耐摩耗性は必要がない事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
成材量の比率・量により強度低下を抑制できる、ハニカ
ム状構造の優位性を見出した。
[0015] Further, when a strong acid is used, the reduction in strength when processing the material into a granular shape, a sheet shape or a honeycomb shape by combining the processing material with other constituent materials should be examined, and a honeycomb type continuous gas adsorption apparatus should be applied. Thus, it was found that abrasion resistance was not required because the material was not a fluidized bed, so that continuous processing was possible even if a certain degree of strength reduction occurred. further,
When phosphoric acid or the like, which is a strong acid, is used as a weak acid, the strength of the constituent material is reduced more strongly. I found an advantage.

【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
質を多孔質吸着基材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 attaching an acidic substance to a porous adsorption substrate.

【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態様は、前記酸性物質がリン酸、
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 substance is phosphoric acid,
It is a phosphate compound.

【0020】本発明の排気ガスの処理材の好ましい実施
態様は、前記多孔質吸着基材が活性炭である。
In a preferred embodiment of the exhaust gas treating material of the present invention, the porous adsorption substrate is activated carbon.

【0021】また、本発明は、酸性物質を多孔質吸着基
材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 onto a porous adsorption substrate into a honeycomb structure.

【0022】さらに、本発明は、塩基性物質を含有する
排気ガスを、酸性物質を多孔質吸着基材に添着してなる
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材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 attaching an acidic substance to a porous adsorbent substrate, and a step of adsorbing the basic substance on the adsorbent. And an exhaust gas treatment apparatus and method including a step of desorbing a basic substance adsorbed on the adsorbent.

【0023】さらに、本発明は、塩基性物質を含有する
排気ガスを、酸性物質を多孔質吸着基材に添着してなる
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
及び該吸着材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 process for bringing an exhaust gas containing a basic substance into contact with an adsorbent obtained by impregnating an acidic substance to a porous adsorbent substrate 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 on a material and a step of desorbing the basic substance adsorbed on the adsorbent.

【0024】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.

【0025】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.

【0026】[0026]

【発明の実施の形態】本発明において、多孔質吸着基材
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 a porous adsorption substrate 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.

【0027】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.

【0028】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、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 to heat treatment, have high heat resistance, have high safety by heating during desorption operation, and have an adsorbing group. It is preferable because it has a high adhesiveness to the material and can be easily attached to the adsorption substrate.

【0029】本発明において、吸着剤を添着する吸着基
材は、多孔質吸着基材であることが必要である。多孔質
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 a porous adsorbent substrate. This is because, if it is porous, excellent adsorbing performance of a basic substance can be exhibited by holding an adsorbent for a basic substance such as ammonia on the porous surface.

【0030】多孔質吸着基材としては、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が、通常、活性炭や
ゼオライト等が好適に用いられる。
The porous adsorbent substrate may be appropriately selected depending on the adsorption performance for the organic compound to be treated, and is not particularly limited. Usually, activated carbon, zeolite, or the like is preferably used.

【0031】中でも、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。
Among them, activated carbon is more preferable because it has a high expression rate of adsorption performance for basic substances due to the impregnated acidic substance, and has a low desorption efficiency because of its low water adsorption performance due to its hydrophobicity. Specifically, coconut shell charcoal,
There is activated carbon such as cellulose, but it is not particularly limited.

【0032】本発明において、多孔質吸着基材に添着す
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、多孔性吸着基材の細孔表面が殆ど添着剤
で被覆され、多孔性吸着基材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。ま
た、強酸を使用した場合に添着量が増えると粒状やシー
ト状やハニカム状の処理エレメントの強度低下が大きく
なり、50重量%を超えると連続使用が難しくなるから
である。
In the present invention, the amount of the acidic substance to be attached to the porous adsorption substrate is preferably 1 to 50% by weight,
-40% by weight is more preferable, and 15-30% by weight is particularly preferable. 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 pore surface of the porous adsorbent substrate is almost covered with the impregnating agent. This is because the adsorptive base material does not sufficiently exhibit the adsorptive performance to the organic compound originally possessed. In addition, when a strong acid is used, an increase in the amount of application causes a large decrease in the strength of the granular, sheet-like, or honeycomb-like processing element, and when it exceeds 50% by weight, continuous use becomes difficult.

【0033】例えば、リン酸を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。
For example, when phosphoric acid is impregnated on 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】本発明において、酸性物質を多孔性吸着基
材へ添着する方法は、吸着基材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。逆にリン酸等はバインダーとし
て作用するため、微粒状炭に添着した場合には微粒状炭
同士が結合し塊となり、流動性を著しく低下させる。
In the present invention, the method of attaching the acidic substance to the porous adsorbent substrate is not particularly limited as long as the acidic substance can be uniformly fixed on the porous surface of the adsorbent substrate. For example, an acidic substance such as phosphoric acid can be easily attached by drying after impregnating the adsorbent in an aqueous phosphoric acid solution because the acidic substance itself acts as a binder. Conversely, since phosphoric acid or the like acts as a binder, when it is impregnated with fine-grained charcoal, the fine-grained charcoal is combined with each other to form a lump, which significantly reduces fluidity.

【0035】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。図1に処理材、およびハニカム構造にしたものの概
略図を示した。
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. FIG. 1 shows a schematic diagram of a treatment material and a honeycomb structure.

【0036】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、酸性物質を多孔質吸着基材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 of the present invention include a step of bringing an exhaust gas containing a basic substance, preferably ammonia, into contact with an adsorbent obtained by impregnating an acidic substance with a porous adsorption substrate; It is necessary to include a step of adsorbing a basic substance on the adsorbent 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.

【0037】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 a malodorous substance such as ammonia and another organic solvent, rather than a simple ammonia gas. The present invention can be applied.

【0038】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装置
及び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-like 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 exhaust gas apparatus and processing 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 may be used, and in particular, It is not limited to these. Also, the desorbed ammonia is, for example,
It is oxidized and decomposed by a combustion device to produce clean air.

【0039】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.

【0040】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ー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
状活性炭との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撹拌した。その後の微粒
状活性炭の破砕状況を目視にて判断した。
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 is determined by an activated carbon material adsorption element Q = 25.0 (vol%) Measurement of treatment performance (removal rate) The treatment performance (η) is measured using an exhaust gas treatment device (FIG. 2). The removal rate is calculated by the following equation. η (%) = (IO) / 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 abrasion 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. The 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 put into 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.

【0041】[0041]

【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1時間乾燥させ、リン酸を30重量%添着した活性炭
を使用したハニカム状吸着素子を得た。吸着材の脱落は
無く良好な結果を得た。次に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。リン酸を添着した活性炭吸着材を用
いる事で、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。
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
For 1 hour to obtain a honeycomb-shaped adsorption element using activated carbon impregnated with 30% by weight of phosphoric acid. Good results were obtained without the adsorbent falling off. Next, 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 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 an ammonia gas is adsorbed and removed by passing 100 ppm ammonia exhaust gas through the adsorption zone. On the other hand, 130 ° C. heated air was blown into the desorption zone at a rate of 1/20 of the air flow to the adsorption zone, and the operation of desorbing ammonia was continuously performed to measure the ammonia treatment performance. did. By using the activated carbon adsorbent impregnated with phosphoric acid, good results were obtained in which the ammonia treatment performance was dramatically improved.

【0042】(実施例2)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%のリン酸第1ナトリウム
水溶液に含浸し、100℃で1時間乾燥させ、リン酸第
1ナトリウムを30重量%添着した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。リン酸第1ナトリウ
ム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100pp
m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。リン酸を添着した活性炭吸着
材を用いる事で、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。
(Example 2) 60% by weight of powdered activated carbon as an adsorbent and Kevlar, glass,
An adsorption element having a honeycomb structure having a wavelength of 3.1 mm and a wave height of 2.1 mm composed of PVA and polyvinyl acetate emulsion of 40% by weight is impregnated with a 30% by weight aqueous solution of sodium phosphate monobasic at 100 ° C. After drying for a time, a honeycomb-shaped adsorption element using activated carbon impregnated with monosodium phosphate at 30% by weight was obtained. 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 monobasic sodium phosphate, the adsorption performance of ammonia 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 apparatus (FIG. 2), and the element is divided into an adsorption zone and a desorption zone.
m and exhausting ammonia to adsorb and remove ammonia, and on the other hand, passing 130 ° C. heated air at 1/20 of the air flow to the desorption zone with respect to the air flow to the adsorption zone to remove ammonia. The desorption operation was continuously performed, and the treatment performance of ammonia was measured. By using the activated carbon adsorbent impregnated with phosphoric acid, good results were obtained in which the ammonia treatment performance was dramatically improved.

【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。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13
0℃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。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)
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 the honeycomb-shaped adsorption element was measured. The ammonia adsorption performance was significantly lower than that of the example. Next, this honeycomb-shaped adsorption element is adapted to an exhaust gas treatment device (FIG. 2),
The device is divided into an adsorption zone and a desorption zone, and an operation of passing 100 ppm of ammonia exhaust gas through the adsorption zone to adsorb and remove ammonia is performed. 13 of 20 airflow
The operation of desorbing ammonia by continuously passing heated air at 0 ° C. was performed, and the treatment performance of ammonia was measured. As a result, the ammonia treatment performance was significantly lower than that of the example.
(Table 1)

【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、ヘキサ
メタリン酸ソーダを30重量%添着した粒状活性炭を使
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 adsorption element having a honeycomb-shaped structure having a thickness of 2 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 adsorption element using granular activated carbon impregnated with 30% by weight of sodium hexametaphosphate. . 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 porosity, which is a characteristic of the adsorbent, affects the adsorption of ammonia by the adsorbent.

【0045】(比較例3)微粒状活性炭に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%添着した微粒状活性炭を得た。これの
流動性および耐摩耗性について測定した。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。
Comparative Example 3 Fine-grained activated carbon was impregnated with a 30% by weight aqueous solution of phosphoric acid and dried at 100 ° C. for 1 hour to obtain fine-grained activated carbon impregnated with 30% by weight of phosphoric acid. Its fluidity and wear 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.

【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
活性炭を使用する事で、吸着材のアンモニア以外の吸着
性能を低下おさえ、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. In particular, the use of phosphoric acid as the inorganic acid and the use of activated carbon as the adsorbent reduce the adsorption performance of the adsorbent other than ammonia, and the adsorption and desorption of ammonia The effect of the treatment is that the treatment performance of ammonia can be made extremely high.

【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 d 口径
A1, A2 Serpentine tube for temperature control B1, B2, B3 Gas washing bottle with common grounding 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 rate Meter F2 Dilution air flow meter 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 d Diameter

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D002 AA13 BA04 BA12 CA05 DA18 DA41 EA08 4G066 AA05B AA05C AA50B AA71D AC12D AC26D BA07 BA36 CA29 DA02 FA12 FA21 FA25 FA28 GA16  ──────────────────────────────────────────────────続 き Continued on the front page F-term (reference) 4D002 AA13 BA04 BA12 CA05 DA18 DA41 EA08 4G066 AA05B AA05C AA50B AA71D AC12D AC26D BA07 BA36 CA29 DA02 FA12 FA21 FA25 FA28 GA16

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】酸性物質を多孔質吸着基材に添着してなる
排気ガスの処理材をハニカム状構造に成形してなること
を特徴とする排気ガスの処理エレメント。
An exhaust gas treatment element characterized in that an exhaust gas treatment material obtained by adhering an acidic substance to a porous adsorption substrate is formed into a honeycomb-like structure.
【請求項2】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記載の排気ガスの処理材及び
処理エレメント。
2. The exhaust gas treatment material and treatment element according to claim 1, wherein the acidic substance is an inorganic acid or an inorganic acid salt.
【請求項3】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乃至2記載のいずれかの排気ガスの
処理材及び処理エレメント。
3. The exhaust gas treatment material and treatment element according to claim 1, wherein the acidic substance is a phosphate compound.
【請求項4】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記載のいずれかの排気ガスの処理材及
び処理エレメント。
4. The exhaust gas treatment material and treatment element according to claim 1, wherein the acidic substance is phosphoric acid.
【請求項5】多孔質吸着基材が活性炭であることを特徴
とする請求項1乃至4記載のいずれかの排気ガスの処理
材及び処理エレメント。
5. The exhaust gas treatment material and treatment element according to claim 1, wherein the porous adsorption substrate is activated carbon.
【請求項6】請求項6記載の処理エレメントに、塩基性
物質を含む排気ガスを接触させる工程、該吸着材に塩基
性物質を吸着させる工程及び該吸着材に吸着している塩
基性物質を脱着させる工程を含むことを特徴とする排気
ガスの処理装置及び処理方法。
6. A step of contacting the treatment element according to claim 6 with an exhaust gas containing a basic substance, a step of adsorbing the basic substance on the adsorbent, and a step of adsorbing the basic substance adsorbed on the adsorbent. An exhaust gas treatment apparatus and method comprising a step of desorption.
【請求項7】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記載の排
気ガスの処理装置及び処理方法。
7. 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8】請求項1乃至7記載のいずれかの排気ガス
に含まれる塩基性物質がアンモニアであることを特徴と
する排気ガスの処理方法。
8. A method for treating exhaust gas according to claim 1, wherein the basic substance contained in the exhaust gas is ammonia.
JP2000240205A 2000-08-08 2000-08-08 Treatment material, treatment element, treatment equipment and treatment process for exhaust gas Withdrawn JP2002045690A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000240205A JP2002045690A (en) 2000-08-08 2000-08-08 Treatment material, treatment element, treatment equipment and treatment process for exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000240205A JP2002045690A (en) 2000-08-08 2000-08-08 Treatment material, treatment element, treatment equipment and treatment process for exhaust gas

Publications (1)

Publication Number Publication Date
JP2002045690A true JP2002045690A (en) 2002-02-12

Family

ID=18731602

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000240205A Withdrawn JP2002045690A (en) 2000-08-08 2000-08-08 Treatment material, treatment element, treatment equipment and treatment process for exhaust gas

Country Status (1)

Country Link
JP (1) JP2002045690A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013078716A (en) * 2011-10-03 2013-05-02 Sumitomo Electric Ind Ltd Gas decomposition electric power generation system
JP2015509832A (en) * 2013-01-19 2015-04-02 デシカント・ローターズ・インターナショナル・プライヴェート・リミテッド Desiccant-supporting honeycomb chemical filter and manufacturing method thereof
JP2018099674A (en) * 2017-10-12 2018-06-28 デシカント・ローターズ・インターナショナル・プライヴェート・リミテッド Desiccant based honeycomb chemical filter and method of manufacture thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013078716A (en) * 2011-10-03 2013-05-02 Sumitomo Electric Ind Ltd Gas decomposition electric power generation system
JP2015509832A (en) * 2013-01-19 2015-04-02 デシカント・ローターズ・インターナショナル・プライヴェート・リミテッド Desiccant-supporting honeycomb chemical filter and manufacturing method thereof
JP2018099674A (en) * 2017-10-12 2018-06-28 デシカント・ローターズ・インターナショナル・プライヴェート・リミテッド Desiccant based honeycomb chemical filter and method of manufacture thereof

Similar Documents

Publication Publication Date Title
Zhou et al. Effect of flue gas component and ash composition on elemental mercury oxidation/adsorption by NH4Br modified fly ash
CA2575482C (en) Catalyst for carbon monoxide removal and method of removing carbon monoxide with the catalyst
EP2731699B1 (en) Use of bromide-containing inorganic salt and activated carbon for reducing mercury emissions from combustion gas streams
US6837917B2 (en) Process for the removal of ethylene oxide from air
US7678182B2 (en) Material and process for the filtration of nitric acid and NO2 from streams of air
JP3684471B2 (en) Bag filter material
CN113304728A (en) Secondary modified carbon-based phosphorus adsorption composite material and preparation method and application thereof
JP2002066255A (en) Treatment material, treatment element, treatment apparatus, and treatment method of waste gas
JP2002045690A (en) Treatment material, treatment element, treatment equipment and treatment process for exhaust gas
JP2002001110A (en) Material, element, device and method for treating exhaust gas
CN100431689C (en) Preparation method of compound absorbent for removing nitrogen oxide
JP2002045688A (en) Treatment material, treatment element, treatment equipment and treatment process for exhaust gas
CA2676548C (en) Filtration media having a chemical reagent
CN105289492B (en) A kind of multi-functional desulfurization denitration demercuration adsorbent and its preparation and application
JP3050139B2 (en) Activated carbon reforming method
JPH11511687A (en) Acid contact enhanced adsorbent particles and methods of making and using same
JP2000237583A (en) Material, element and method for treating waste gas
JP2012030199A (en) Method for treating gas containing nitrogen oxide
JPS6219241A (en) Absorber for nitrogen oxide and sulfur oxide
CN112107992A (en) Harmful gas removing medium and preparation method thereof
JP3198107B2 (en) Adsorbent and method for producing the same
Kang et al. Study of mercury-adsorption behavior in the exhaust gas of KI-impregnated ACF
TWI749754B (en) Metal catalyst and its preparation and application for the treatment of acetone
RU2275330C2 (en) Method for preparing chemosorbent
JP3206107B2 (en) Air purifier

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20070717

A761 Written withdrawal of application

Free format text: JAPANESE INTERMEDIATE CODE: A761

Effective date: 20080627