JP2001293368A - Hydrocarbon adsorbent and method for adsorbing and removing hydrocarbon - Google Patents
Hydrocarbon adsorbent and method for adsorbing and removing hydrocarbonInfo
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- JP2001293368A JP2001293368A JP2000117187A JP2000117187A JP2001293368A JP 2001293368 A JP2001293368 A JP 2001293368A JP 2000117187 A JP2000117187 A JP 2000117187A JP 2000117187 A JP2000117187 A JP 2000117187A JP 2001293368 A JP2001293368 A JP 2001293368A
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- adsorbent
- zeolite
- hydrocarbon
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- alkali metal
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Abstract
(57)【要約】
【課題】炭化水素の吸着容量及び吸着保持力に優れ、且
つその炭化水素の吸着性能が処理ガスの雰囲気に影響さ
れることのない高耐熱性の炭化水素の吸着剤を提供す
る。
【解決手段】アルカリ金属を含有し、アルカリ土類金属
及び遷移金属を含有しないゼオライトからなる炭化水素
吸着剤を、処理ガスに接触させ、炭化水素の吸着除去を
行う。(57) [Problem] To provide a highly heat-resistant hydrocarbon adsorbent which is excellent in hydrocarbon adsorption capacity and adsorption holding power and whose hydrocarbon adsorption performance is not affected by the atmosphere of the processing gas. provide. SOLUTION: A hydrocarbon adsorbent comprising zeolite containing an alkali metal and not containing an alkaline earth metal and a transition metal is brought into contact with a processing gas to adsorb and remove the hydrocarbon.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、処理ガス中、例え
ば内燃機関より排出される排ガス中に含まれる炭化水素
(以下HCとする)を浄化する吸着剤及びHCの吸着除
去方法に関するものであり、例えば自動車などの内燃機
関から排出される排ガス中のHC吸着除去等に適用する
ことができる。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an adsorbent for purifying hydrocarbons (hereinafter referred to as HC) contained in a processing gas, for example, exhaust gas discharged from an internal combustion engine, and a method for adsorbing and removing HC. For example, the present invention can be applied to, for example, adsorption and removal of HC in exhaust gas discharged from an internal combustion engine such as an automobile.
【0002】[0002]
【従来の技術】自動車等の内燃機関から排出されるHC
を含有する排ガスの浄化において、三元触媒を用いて、
排ガスと接触させる方法が実用化されている。しかし、
エンジン始動時においては、排ガス中のHC濃度が高い
ことに加えて、三元触媒が作動する温度に達していない
ため、HCは浄化されずにそのまま排出される。2. Description of the Related Art HC emitted from an internal combustion engine of an automobile or the like
In the purification of exhaust gas containing, using a three-way catalyst,
A method of contacting with exhaust gas has been put to practical use. But,
When the engine is started, HC is discharged without being purified because the HC concentration in the exhaust gas is high and the temperature does not reach the temperature at which the three-way catalyst operates.
【0003】低温時の排ガスからのHC浄化に対し、特
開平2−135126号公報ではHCを吸着浄化するこ
とを目的として、Y型ゼオライト及びモルデナイトのゼ
オライトをコートしたモノリス担体の一部に1種以上の
金属を担持したHC吸着剤を用いた排ガス浄化装置が提
案されている。この他にもゼオライトを構成成分とした
HC吸着剤が数多く提案されている。例えば、特開平6
−126165号公報ではAgを担持した分子篩、特開
平7−185326号公報ではアルカリ金属、アルカリ
土類金属のうちの1種以上の金属、及びAg、分子篩か
ら構成されたHC吸着剤が提案されている。また、特開
平6−210165号公報ではPdとゼオライトから構
成される吸着剤、特開平6−210163号公報ではC
uを含有したゼオライト、特開平5−31359号公報
ではSiO2/Al2O3モル比が40以上のゼオライト
が提案されている。更に、特開平11―192427号
公報ではSiO2/Al2O3モル比が500以上のZS
M−5よりなる第1ゼオライトと、SiO2/Al2O3
モル比が200以上のY型ゼオライトよりなる第2ゼオ
ライトから構成したHC吸着剤が提案されている。For the purpose of purifying HC from exhaust gas at low temperatures, Japanese Patent Application Laid-Open No. Hei 2-135126 discloses one type of monolithic carrier coated with Y-type zeolite and mordenite zeolite for the purpose of adsorbing and purifying HC. An exhaust gas purifying apparatus using the HC adsorbent carrying the above-mentioned metals has been proposed. Many other HC adsorbents containing zeolite as a component have been proposed. For example, Japanese Unexamined Patent Publication
JP-126165 proposes a molecular sieve carrying Ag, and JP-A-7-185326 proposes an HC adsorbent composed of Ag and a molecular sieve, one or more of an alkali metal and an alkaline earth metal. I have. JP-A-6-210165 discloses an adsorbent composed of Pd and zeolite, and JP-A-6-210163 discloses C-adsorbent.
zeolite containing u, in JP-A 5-31359 discloses SiO 2 / Al 2 O 3 molar ratio has been proposed more than 40 zeolite. Further, JP-A-11-192427 discloses a ZS having a SiO 2 / Al 2 O 3 molar ratio of 500 or more.
A first zeolite composed of M-5 and SiO 2 / Al 2 O 3
An HC adsorbent composed of a second zeolite composed of a Y-type zeolite having a molar ratio of 200 or more has been proposed.
【0004】[0004]
【発明が解決しようとする課題】近年、環境問題が大き
くクローズアップされ、HC排出量の低減技術の向上が
望まれている。自動車等の内燃機関から排出される排ガ
スから、HC吸着剤を用いて吸着浄化する場合、吸着し
たHCを浄化する必要がある。吸着HCを三元触媒で直
接浄化するためには、三元触媒の作動温度まで排ガス中
のHCを吸着保持できる吸着剤が要求されるが、上記の
従来技術に開示されている吸着剤ではHCの吸着保持力
が不十分であった。In recent years, environmental problems have been greatly highlighted, and there has been a demand for an improved technique for reducing the amount of HC emission. In the case of purifying the exhaust gas discharged from an internal combustion engine of an automobile or the like using an HC adsorbent, it is necessary to purify the adsorbed HC. In order to directly purify the adsorbed HC with the three-way catalyst, an adsorbent capable of adsorbing and holding the HC in the exhaust gas up to the operating temperature of the three-way catalyst is required. Had insufficient adsorption holding power.
【0005】また、内燃機関の排ガスは、運転状況によ
り酸化雰囲気(リーン)から還元雰囲気(リッチ)まで
の幅広い状態をとり、排ガスの温度は600℃以上にも
達する。そのため、吸着剤は排ガスの雰囲気に影響され
ず、高温に晒された後でも十分な吸着容量を有し、かつ
十分な吸着保持力を有することが必要である。即ち、い
ずれの排ガス雰囲気におても耐熱性の高い吸着性能を有
する吸着剤である必要がある。Further, the exhaust gas of the internal combustion engine takes a wide range from an oxidizing atmosphere (lean) to a reducing atmosphere (rich) depending on the operating conditions, and the temperature of the exhaust gas reaches 600 ° C. or more. Therefore, it is necessary that the adsorbent is not affected by the atmosphere of the exhaust gas, has a sufficient adsorption capacity even after being exposed to a high temperature, and has a sufficient adsorption holding power. That is, the adsorbent must have high heat-resistant adsorption performance in any exhaust gas atmosphere.
【0006】本発明の目的は、以上のような従来技術の
問題点を解決する為になされたものであり、HCの吸着
容量及び吸着保持力に優れ、且つそのHCの吸着性能が
処理ガスの雰囲気に影響されることのない高耐熱性の吸
着剤、及びその吸着剤を用いて処理ガス中に含有される
HCを吸着除去する方法を提供するところにある。SUMMARY OF THE INVENTION An object of the present invention is to solve the above-mentioned problems of the prior art, and is excellent in the HC adsorption capacity and adsorption holding power, and the HC adsorption performance of the process gas. An object of the present invention is to provide a highly heat-resistant adsorbent which is not affected by the atmosphere, and a method for adsorbing and removing HC contained in a processing gas using the adsorbent.
【0007】[0007]
【課題を解決するするための手段】本発明者は、上記課
題に対して、HCの吸着−脱離特性を鋭意検討した結
果、アルカリ金属を含有するゼオライトが、これまでに
開示されたHC吸着剤に比べて、HCの吸着保持力に優
れ、更には処理ガスの雰囲気に影響されることなく、高
温に晒された後でも高い吸着性能を有することを見出し
本発明を完成するに至った。In order to solve the above-mentioned problems, the present inventors have intensively studied the adsorption-desorption characteristics of HC. As a result, the present invention was found to be excellent in the ability to retain and adsorb HC, and to have high adsorption performance even after being exposed to a high temperature, without being affected by the atmosphere of the processing gas.
【0008】即ち本発明は、アルカリ金属を含有し、ア
ルカリ土類金属及び遷移金属を含有しないゼオライトか
らなることを特徴とする、炭化水素吸着剤である。また
本発明は、そのような炭化水素吸着剤を処理ガスに接触
させることを特徴とする、炭化水素の吸着除去方法であ
る。以下、本発明を詳細に説明する。[0008] That is, the present invention is a hydrocarbon adsorbent comprising a zeolite containing an alkali metal and not containing an alkaline earth metal and a transition metal. The present invention is also a method for adsorbing and removing hydrocarbons, which comprises contacting such a hydrocarbon adsorbent with a processing gas. Hereinafter, the present invention will be described in detail.
【0009】本発明の吸着剤は、アルカリ金属を含有
し、アルカリ土類金属及び遷移金属を含有しないゼオラ
イトであるとが必須である。一般的にゼオライトは、 xM2/nO・Al2O3・ySiO2・zH2O (但し、nは陽イオンMの原子価、xは0〜2.5の範
囲の数、yは2以上の数、zは0以上の数である)の組
成を有し、天然品及び合成品として得られる。また、ゼ
オライトは、X線回折等でみられる結晶構造、及び細孔
径、細孔構造等から分類、特定することができる。It is essential that the adsorbent of the present invention is a zeolite containing an alkali metal and not containing an alkaline earth metal and a transition metal. Typically zeolites, xM 2 / n O · Al 2 O 3 · ySiO 2 · zH 2 O ( where, n is the valence of the cation M, x is a number in the range of 0 to 2.5, y is 2 The above number, z is a number of 0 or more), and can be obtained as natural products and synthetic products. In addition, zeolite can be classified and specified based on the crystal structure observed by X-ray diffraction or the like, the pore diameter, the pore structure, and the like.
【0010】本発明に係るゼオライトのSiO2/Al2
O3モル比は、特に限定されないが、吸着剤の耐熱性を
十分に高めるために、好ましくは10以上が良く、より
好ましくは20以上である。[0010] The zeolite of the present invention is SiO 2 / Al 2
The O 3 molar ratio is not particularly limited, but is preferably 10 or more, more preferably 20 or more, in order to sufficiently increase the heat resistance of the adsorbent.
【0011】本発明に用いられるゼオライトの構造は特
に限定されないが、公知のFER、MFI、MOR、B
EA、FAU構造のゼオライトを用いることが好まし
い。より好ましくはMFI、BEAが良い。また、単一
構造のゼオライトに限らず、2種以上のゼオライトを混
合して用いても良い。Although the structure of the zeolite used in the present invention is not particularly limited, known FER, MFI, MOR, B
It is preferable to use a zeolite having an EA or FAU structure. More preferably, MFI and BEA are good. Further, the zeolite is not limited to a single-structure zeolite, and two or more zeolites may be used in combination.
【0012】ゼオライトの製造方法も特に限定されず、
一般的に知られているシリカ源及びアルミナ源をアルカ
リ溶液中に分散させ、水熱合成する方法等を採用するこ
とができる。更には製造原料中に有機硬化剤等を添加し
て製造することもできる。The method for producing the zeolite is not particularly limited, either.
A commonly known method of dispersing a silica source and an alumina source in an alkaline solution and performing hydrothermal synthesis can be employed. Further, it can be produced by adding an organic curing agent or the like to the production raw material.
【0013】本発明の吸着剤は、アルカリ金属を含有
し、アルカリ土類金属及び遷移金属を含有しないゼオラ
イトからなるものである。ゼオライトに含有させるアル
カリ金属は特に限定はないが、例えばK,Rb,Cs等
が挙げられ、これらアルカリ金属の少なくとも一種以上
を含有していれば良く、複数種含有していてもよい。H
Cの吸着保持力を十分に高めるために、好ましくはCs
が良い。アルカリ金属を含有させるために用いる原料に
特に制限はなく、アルカリ金属の硝酸塩、硫酸塩、酢酸
塩、塩化物等を用いることができる。上記ゼオライトに
アルカリ金属を含有させる方法としては、公知のイオン
交換法、含浸担持法、蒸発乾固法、物理混合法が採用で
きる。また、ゼオライトを合成する際に、アルカリ金属
原料を添加して含有させても良い。本発明の吸着剤の吸
着性能を十分に高めるために、含有するアルカリ金属が
イオン交換状態であることが望ましく、そのためイオン
交換法によってアルカリ金属を含有させることが好まし
い。ゼオライトに含有させるアルカリ金属の含有量は特
に制限されないが、HCの吸着容量、吸着保持力をを十
分に高めるためには、ゼオライトに対してアルカリ金属
原子が0.1〜30重量%の範囲で良く、より好ましく
は2〜20重量%の範囲が良い。The adsorbent of the present invention comprises a zeolite containing an alkali metal and not containing an alkaline earth metal and a transition metal. The alkali metal contained in the zeolite is not particularly limited, but includes, for example, K, Rb, Cs and the like. It is sufficient that at least one of these alkali metals is contained, and a plurality of these may be contained. H
In order to sufficiently increase the adsorption and holding power of C, preferably Cs
Is good. There are no particular restrictions on the raw materials used to contain the alkali metal, and nitrates, sulfates, acetates, chlorides, and the like of alkali metals can be used. As a method for allowing the zeolite to contain an alkali metal, a known ion exchange method, impregnation-supporting method, evaporation to dryness method, and physical mixing method can be adopted. When synthesizing the zeolite, an alkali metal raw material may be added and contained. In order to sufficiently enhance the adsorption performance of the adsorbent of the present invention, it is desirable that the contained alkali metal is in an ion-exchanged state. Therefore, it is preferable that the alkali metal be contained by an ion-exchange method. The content of the alkali metal contained in the zeolite is not particularly limited. However, in order to sufficiently increase the HC adsorption capacity and adsorption holding power, the content of the alkali metal atom in the zeolite is in the range of 0.1 to 30% by weight based on the zeolite. And more preferably in the range of 2 to 20% by weight.
【0014】上記方法によりアルカリ金属を含有させた
ゼオライトは熱処理(焼成)して用いていも良い。その
熱処理条件も特に限定されない。通常400〜1000
℃の範囲の温度、0.5〜10時間の範囲の時間で処理
することができる。The zeolite containing an alkali metal by the above method may be used after heat treatment (calcination). The heat treatment conditions are not particularly limited. Usually 400 to 1000
The treatment can be carried out at a temperature in the range of ° C and a time in the range of 0.5 to 10 hours.
【0015】以上のようにして、本発明のHC吸着剤を
製造することができる。本発明の吸着剤は、シリカ、ア
ルミナ及び粘土鉱物等のバインダーと混合し成形して使
用することもできる。粘土鉱物としては、カオリン、ア
タパルガイト、モンモリロナイト、ベントナイト、アロ
フェン、セピオライト等を挙げることができる。またコ
ージェライト製あるいは金属製のハニカム状基材にウォ
ッシュコートして使用することもできる。ウォッシュコ
ートする場合、ハニカム状基材にゼオライトをコートし
た後にアルカリ金属を含有させる方法、予めゼオライト
にアルカリ金属を含有させた後に、ハニカム状基材にコ
ートする方法などが採用できる。As described above, the HC adsorbent of the present invention can be produced. The adsorbent of the present invention can be mixed with a binder such as silica, alumina, and clay minerals and then molded and used. Examples of the clay mineral include kaolin, attapulgite, montmorillonite, bentonite, allophane, sepiolite and the like. Further, it can be used by wash-coating a cordierite or metal honeycomb substrate. In the case of wash coating, a method of coating a honeycomb substrate with zeolite and then containing an alkali metal, a method of preliminarily adding zeolite to an alkali metal and then coating the honeycomb substrate with the zeolite can be employed.
【0016】上記のような本発明のHC吸着剤に処理ガ
スを接触させることにより、処理ガス中のHCを吸着除
去することができる。処理ガスとしてはガソリンエンジ
ン自動車、ディーゼルエンジン自動車等の内燃機関の排
ガスが具体的に例示される。更に上記処理ガスには、H
C以外に一酸化炭素、二酸化炭素、水素、窒素、酸素、
硫黄化合物、窒素酸化物、水等が含まれていても良い。By bringing the treatment gas into contact with the HC adsorbent of the present invention as described above, the HC in the treatment gas can be adsorbed and removed. Specific examples of the processing gas include exhaust gas from internal combustion engines such as gasoline engine vehicles and diesel engine vehicles. Further, the processing gas includes H
In addition to C, carbon monoxide, carbon dioxide, hydrogen, nitrogen, oxygen,
It may contain sulfur compounds, nitrogen oxides, water and the like.
【0017】本発明で処理されるガスに含まれるHCの
種類は特に限定されず、パラフィン、オレフィン、芳香
族化合物等を挙げることができる。パラフィン、オレフ
ィンとしては、炭素数で1〜20の直鎖状及び分岐状の
HC、芳香族化合物としてはベンゼン、トルエン、ナフ
タレン及びその誘導体等が例示される。またケトン、ア
ルデヒドなどの含酸素有機化合物やアミンなどの含窒素
化合物でも良い。更には、上記のHCから選ばれる2種
以上のHCが混合されている状態でも有効である。The type of HC contained in the gas to be treated in the present invention is not particularly limited, and examples thereof include paraffin, olefin, and aromatic compound. Examples of paraffin and olefin include linear and branched HC having 1 to 20 carbon atoms, and examples of aromatic compounds include benzene, toluene, naphthalene and derivatives thereof. Also, oxygen-containing organic compounds such as ketones and aldehydes and nitrogen-containing compounds such as amines may be used. Further, it is effective even in a state where two or more HCs selected from the above-mentioned HCs are mixed.
【0018】排ガス中のHC濃度は特に限定されない
が、メタン換算で0.001〜10体積%が好ましく、
より好ましくは0.001〜5体積%である。The HC concentration in the exhaust gas is not particularly limited, but is preferably 0.001 to 10% by volume in terms of methane.
More preferably, the content is 0.001 to 5% by volume.
【0019】排ガス中のHCを吸着除去する際の空間速
度及び温度は特に限定されないが、空間速度:100〜
500,000hr-1、温度−30〜200℃であるこ
とが好ましい。The space velocity and temperature at the time of adsorbing and removing HC in the exhaust gas are not particularly limited.
Preferably, the temperature is 500,000 hr -1 and the temperature is -30 to 200 ° C.
【0020】[0020]
【実施例】以下本発明を実施例により更に詳細に説明す
るが、本発明は、これらの実施例に何ら限定されるもの
ではない。EXAMPLES The present invention will be described in more detail with reference to the following Examples, but it should not be construed that the present invention is limited to these Examples.
【0021】<実施例1>吸着剤1の調製 SiO2/Al2O3モル比が40の東ソー製NH4型ZS
M−5(商品名:HSZ−840NHA)を、塩化セシ
ウム水溶液中に添加し、80℃のイオン交換操作を2回
行った。イオン交換後、固液分離し、十分量の純水で洗
浄後、110℃で20時間乾燥して、吸着剤1を得た。
吸着剤1のCs含有量を原子吸光分析により分析したと
ころ、ゼオライトに対して9.6重量%であった。Example 1 Preparation of Adsorbent 1 NH 4 type ZS manufactured by Tosoh having a SiO 2 / Al 2 O 3 molar ratio of 40
M-5 (trade name: HSZ-840NHA) was added to the cesium chloride aqueous solution, and the ion exchange operation at 80 ° C. was performed twice. After ion exchange, solid-liquid separation was performed, and the solid was washed with a sufficient amount of pure water.
When the Cs content of the adsorbent 1 was analyzed by atomic absorption spectroscopy, it was 9.6% by weight based on zeolite.
【0022】<実施例2>吸着剤2の調製 SiO2/Al2O3モル比が37の東ソー製βゼオライ
ト(商品名:HSZ−940NHA)を600℃で焼成
して、H型β(BEA−1)を得た。Example 2 Preparation of Adsorbent 2 β-zeolite (trade name: HSZ-940NHA) manufactured by Tosoh having a molar ratio of SiO 2 / Al 2 O 3 of 37 was calcined at 600 ° C. to obtain H-type β (BEA). -1) was obtained.
【0023】NH4型ZSM−5をBEA−1に替えた
こと以外は、実施例1と同様な操作を行って、吸着剤2
を得た。吸着剤2のCs含有量を原子吸光分析により分
析したところ、ゼオライトに対して10.3重量%であ
った。Except that the NH 4 type ZSM-5 was changed to BEA-1, the same operation as in Example 1 was performed to obtain adsorbent 2
I got When the Cs content of the adsorbent 2 was analyzed by atomic absorption analysis, it was 10.3% by weight with respect to the zeolite.
【0024】<実施例3>吸着剤3の調製 SiO2/Al2O3モル比が23の東ソー製Na型ZS
M−5(商品名:HSZ−820NAA)を塩化アンモ
ニウム水溶液中でイオン交換し、引き続き固液分離、洗
浄、乾燥して、NH4型ZSM−5(MFI−1)を得
た。実施例1のNH4型ZSM−5を、MFI−1に替
えたこと以外は、実施例1と同様な操作を行って、吸着
剤3を得た。吸着剤3のCs含有量を原子吸光分析によ
り分析したところ、ゼオライトに対して15.2重量%
であった。<Example 3> Preparation of adsorbent 3 Na type ZS manufactured by Tosoh having a SiO 2 / Al 2 O 3 molar ratio of 23
M-5 (trade name: HSZ-820NAA) was ion-exchanged in an aqueous ammonium chloride solution, followed by solid-liquid separation, washing and drying to obtain NH 4 type ZSM-5 (MFI-1). An adsorbent 3 was obtained by performing the same operation as in Example 1 except that the NH 4 type ZSM-5 in Example 1 was changed to MFI-1. When the Cs content of the adsorbent 3 was analyzed by atomic absorption spectroscopy, it was 15.2% by weight based on zeolite.
Met.
【0025】<実施例4>吸着剤4の調製 NH4型ZSM−5を、SiO2/Al2O3モル比が72
の東ソー製H型ZSM−5(商品名:HSZ−860H
OA)に替えたこと以外は、実施例1と同様な操作を行
って、吸着剤4を得た。吸着剤4のCs含有量を原子吸
光分析により分析したところ、ゼオライトに対して5.
7重量%であった。Example 4 Preparation of Adsorbent 4 NH 4 type ZSM-5 was prepared by mixing SiO 2 / Al 2 O 3 at a molar ratio of 72.
Tosoh H type ZSM-5 (trade name: HSZ-860H)
Adsorbent 4 was obtained by performing the same operation as in Example 1 except that OA) was used. The Cs content of the adsorbent 4 was analyzed by atomic absorption spectroscopy.
7% by weight.
【0026】<実施例5>吸着剤5の調製 塩化セシウム水溶液を硝酸カリウム水溶液にしたこと以
外は、実施例1と同様な操作でK交換を行った。イオン
交換後、固液分離し、十分量の純水で洗浄後、110℃
で20時間乾燥して、吸着剤5を得た。吸着剤5のK含
有量を原子吸光分析により分析したところ、ゼオライト
に対して3.0重量%であった。<Example 5> Preparation of adsorbent 5 K exchange was performed in the same manner as in Example 1 except that the aqueous solution of cesium chloride was changed to an aqueous solution of potassium nitrate. After ion exchange, solid-liquid separation, washing with a sufficient amount of pure water, 110 ° C
For 20 hours to obtain the adsorbent 5. When the K content of the adsorbent 5 was analyzed by atomic absorption spectroscopy, it was 3.0% by weight with respect to the zeolite.
【0027】<比較例1>比較吸着剤1の調製 実施例1で用いたNH4型ZSM−5を500℃で1時
間空気焼成してH型ZSM−5とし、比較吸着剤1とし
た。Comparative Example 1 Preparation of Comparative Adsorbent 1 The NH 4 type ZSM-5 used in Example 1 was calcined in air at 500 ° C. for 1 hour to obtain H type ZSM-5, which was used as Comparative Adsorbent 1.
【0028】<比較例2>比較吸着剤2の調製 SiO2/Al2O3モル比が2100の東ソー製H型Z
SM−5(商品名:HSZ−890HOA)を、600
℃で1時間空気焼成して、比較吸着剤2とした。<Comparative Example 2> Preparation of Comparative Adsorbent 2 Tosoh H-type Z having a SiO 2 / Al 2 O 3 molar ratio of 2100
SM-5 (trade name: HSZ-890HOA), 600
The mixture was calcined in air at 1 ° C. for 1 hour to obtain Comparative Adsorbent 2.
【0029】<比較例3>比較吸着剤3の調製 SiO2/Al2O3モル比が360の東ソー製H型Y型
ゼオライト(商品名:HSZ−390HUA)を、50
0℃で1時間空気焼成して、比較吸着剤3とした。<Comparative Example 3> Preparation of Comparative Adsorbent 3 H-type and Y-type zeolite (trade name: HSZ-390HUA) manufactured by Tosoh having a SiO 2 / Al 2 O 3 molar ratio of 360
The resultant was calcined in air at 0 ° C. for 1 hour to obtain Comparative Adsorbent 3.
【0030】<比較例4>比較吸着剤4の調製 塩化セシウム水溶液を硝酸銀水溶液にしたこと以外は、
実施例1と同様なイオン交換操作でAg交換を行った。
イオン交換後、固液分離し、十分量の純水で洗浄後、1
10℃で20時間乾燥して、比較吸着剤4を得た。比較
吸着剤4のAg含有量をICP発光分析により分析した
ところ、ゼオライトに対して5.2重量%であった。<Comparative Example 4> Preparation of Comparative Adsorbent 4 Except that the cesium chloride aqueous solution was changed to a silver nitrate aqueous solution,
Ag exchange was performed by the same ion exchange operation as in Example 1.
After ion exchange, solid-liquid separation, washing with a sufficient amount of pure water,
After drying at 10 ° C. for 20 hours, Comparative Adsorbent 4 was obtained. The Ag content of the comparative adsorbent 4 was analyzed by ICP emission spectrometry, and it was 5.2% by weight based on zeolite.
【0031】<比較例5>比較吸着剤5の調製 SiO2/Al2O3モル比が40の東ソー製NH4型ZS
M−5(商品名:HSZ−840NHA)を、酢酸銅水
溶液中に添加し、続いて該スラリーにアンモニア水を添
加してpHを10.5に調整した。その後、30℃で2
0時間のイオン交換操作でCu交換を行った。上記のC
u交換を2回行った後、固液分離し、十分量の純水で洗
浄後、110℃で20時間乾燥して、比較吸着剤5を得
た。比較吸着剤5のCu含有量をICP発光分析により
分析したところ、ゼオライトに対して2.6重量%であ
った。Comparative Example 5 Preparation of Comparative Adsorbent 5 NH 4 type ZS manufactured by Tosoh having a SiO 2 / Al 2 O 3 molar ratio of 40
M-5 (trade name: HSZ-840NHA) was added to an aqueous copper acetate solution, and subsequently, aqueous ammonia was added to the slurry to adjust the pH to 10.5. Then, at 30 ° C, 2
Cu exchange was performed by an ion exchange operation for 0 hours. C above
After performing u exchange twice, solid-liquid separation was performed, washed with a sufficient amount of pure water, and dried at 110 ° C. for 20 hours to obtain Comparative Adsorbent 5. When the Cu content of the comparative adsorbent 5 was analyzed by ICP emission spectrometry, it was 2.6% by weight based on the zeolite.
【0032】<比較例6>比較吸着剤6の調製 塩化セシウム水溶液を硝酸マグネシウム水溶液にしたこ
と以外は、実施例1と同様な操作でMg交換を行った。
イオン交換後、固液分離し、十分量の純水で洗浄後、1
10℃で20時間乾燥して、比較吸着剤6を得た。比較
吸着剤6のMg含有量をICP発光分析により分析した
ところ、ゼオライトに対して0.2重量%であった。Comparative Example 6 Preparation of Comparative Adsorbent 6 The procedure of Example 1 was repeated except that the aqueous solution of cesium chloride was replaced with an aqueous solution of magnesium nitrate.
After ion exchange, solid-liquid separation, washing with a sufficient amount of pure water,
After drying at 10 ° C. for 20 hours, Comparative Adsorbent 6 was obtained. When the Mg content of the comparative adsorbent 6 was analyzed by ICP emission analysis, it was 0.2% by weight based on the zeolite.
【0033】<比較例7>比較吸着剤7の調製 塩化セシウム水溶液を酢酸カルシウム水溶液にしたこと
以外は、実施例1と同様な操作でCa交換を行った。イ
オン交換後、固液分離し、十分量の純水で洗浄後、11
0℃で20時間乾燥して、比較吸着剤7を得た。比較吸
着剤7のCa含有量をICP発光分析により分析したと
ころ、ゼオライトに対して0.3重量%であった。<Comparative Example 7> Preparation of Comparative Adsorbent 7 Ca exchange was performed in the same manner as in Example 1 except that the aqueous cesium chloride solution was changed to an aqueous calcium acetate solution. After ion exchange, solid-liquid separation, washing with a sufficient amount of pure water,
After drying at 0 ° C. for 20 hours, Comparative Adsorbent 7 was obtained. When the Ca content of the comparative adsorbent 7 was analyzed by ICP emission analysis, it was 0.3% by weight with respect to the zeolite.
【0034】<比較例8>比較吸着剤8の調製 塩化セシウム水溶液を酢酸亜鉛水溶液にしたこと以外
は、実施例1と同様な操作でZn交換を行った。イオン
交換後、固液分離し、十分量の純水で洗浄後、110℃
で20時間乾燥して、比較吸着剤8を得た。比較吸着剤
8のZn含有量をICP発光分析により分析したとこ
ろ、ゼオライトに対して2.0重量%であった。Comparative Example 8 Preparation of Comparative Adsorbent 8 Zn exchange was carried out in the same manner as in Example 1 except that the aqueous solution of cesium chloride was changed to an aqueous solution of zinc acetate. After ion exchange, solid-liquid separation, washing with a sufficient amount of pure water, 110 ° C
For 20 hours to obtain Comparative Adsorbent 8. When the Zn content of the comparative adsorbent 8 was analyzed by ICP emission spectrometry, it was 2.0% by weight based on zeolite.
【0035】<比較例9>比較吸着剤の調製 モリブデンがゼオライトに対して2重量%となるよう
に、実施例1で用いたNH4型ZSM−5をモリブデン
酸アンモニウム水溶液中に添加し、蒸発乾固法でMo担
持を行った。Mo担持後、110℃で20時間乾燥し
て、比較吸着剤9を得た。Comparative Example 9 Preparation of Comparative Adsorbent The NH 4 type ZSM-5 used in Example 1 was added to an aqueous solution of ammonium molybdate such that molybdenum was 2% by weight based on zeolite, and evaporated. Mo was supported by a drying method. After carrying Mo, it was dried at 110 ° C. for 20 hours to obtain Comparative Adsorbent 9.
【0036】<比較例10>比較吸着剤10の調製 タングステンがゼオライトに対して2重量%となるよう
に、実施例1で用いたNH4型ZSM−5をタングステ
ン酸アンモニウム水溶液中に添加し、蒸発乾固法でW担
持を行った。W担持後、110℃で20時間乾燥して、
比較吸着剤10を得た。Comparative Example 10 Preparation of Comparative Adsorbent 10 The NH 4 type ZSM-5 used in Example 1 was added to an aqueous solution of ammonium tungstate so that the amount of tungsten was 2% by weight based on zeolite. W was carried by the evaporation to dryness method. After supporting W, dried at 110 ° C. for 20 hours,
Comparative adsorbent 10 was obtained.
【0037】<比較例11>比較吸着剤11の調製 NH4型ZSM−5をNa型ZSM−5(SiO2/Al
2O3=40)に替えたこと以外は、比較例4と同様な操
作でAg交換を行った。イオン交換後、固液分離し、十
分量の純水で洗浄後、110℃で20時間乾燥して、比
較吸着剤11を得た。比較吸着剤11のAg及びNa含
有量をICP発光分析により分析したところ、ゼオライ
トに対してAgが4.7重量%で、Naが0.7重量%
あった。Comparative Example 11 Preparation of Comparative Adsorbent 11 NH 4 type ZSM-5 was replaced with Na type ZSM-5 (SiO 2 / Al
Except that instead of the 2 O 3 = 40), were Ag exchanged by the same procedure as Comparative Example 4. After ion exchange, solid-liquid separation was performed, washed with a sufficient amount of pure water, and dried at 110 ° C. for 20 hours to obtain Comparative Adsorbent 11. When the Ag and Na contents of the comparative adsorbent 11 were analyzed by ICP emission spectrometry, Ag was 4.7% by weight and Na was 0.7% by weight with respect to the zeolite.
there were.
【0038】<比較例12>比較吸着剤12の調製 NH4型ZSM−5をNa型βゼオライト(SiO2/A
l2O3=37)に替えたこと以外は、比較例4と同様な
操作でAg交換を行った。イオン交換後、固液分離し、
十分量の純水で洗浄後、110℃で20時間乾燥して、
比較吸着剤12を得た。比較吸着剤12のAg及びNa
含有量をICP発光分析により分析したところ、ゼオラ
イトに対してAgが4.5重量%で、Naが0.9重量
%あった。Comparative Example 12 Preparation of Comparative Adsorbent 12 NH 4 type ZSM-5 was converted to Na type β zeolite (SiO 2 / A).
Ag exchange was carried out in the same manner as in Comparative Example 4, except that (I 2 O 3 = 37). After ion exchange, solid-liquid separation
After washing with a sufficient amount of pure water, drying at 110 ° C. for 20 hours,
Comparative adsorbent 12 was obtained. Ag and Na of comparative adsorbent 12
When the contents were analyzed by ICP emission spectrometry, Ag was 4.5% by weight and Na was 0.9% by weight based on the zeolite.
【0039】<HC吸着除去試験>吸着剤1〜5及び比
較吸着剤1〜12のHC吸着除去特性を以下の方法で評
価した。所定の試料を空気流通下、500℃で前処理
し、室温まで冷却した。次いで、表1の組成のモデル排
ガスを室温下、ガス流速2000ml/minで吸着剤
に接触させた。この時の空間速度は120,000hr
-1であった。モデル排ガス中のHC吸着が飽和した後
に、表1のモデル排ガスからHCだけを除いたガスを吸
着剤に導入し、気相に残存するHCを除去した。その
後、表2のモデル排ガスからHCだけを除いたガスを吸
着剤に接触させながら、吸着剤を10℃/minの昇温
速度で昇温させ、吸着剤から脱離するHCを水素炎イオ
ン化検出器(FID)を備えたガスクロマトグラフによ
り、連続的に定量分析し、HC脱離スペクトルよりHC
の吸着性能を評価した。<HC adsorption removal test> The HC adsorption removal characteristics of the adsorbents 1 to 5 and the comparative adsorbents 1 to 12 were evaluated by the following method. A predetermined sample was pretreated at 500 ° C. in a flowing air and cooled to room temperature. Next, the model exhaust gas having the composition shown in Table 1 was brought into contact with the adsorbent at room temperature at a gas flow rate of 2000 ml / min. The space velocity at this time is 120,000 hr
It was -1 . After the adsorption of HC in the model exhaust gas was saturated, a gas obtained by removing only HC from the model exhaust gas in Table 1 was introduced into the adsorbent to remove HC remaining in the gas phase. Thereafter, the adsorbent was heated at a rate of 10 ° C./min while contacting a gas obtained by removing only HC from the model exhaust gas shown in Table 2 with the adsorbent, and HC desorbed from the adsorbent was detected by flame ionization. Quantitative analysis is continuously performed by a gas chromatograph equipped with a FID, and HC
Was evaluated for adsorption performance.
【0040】HCの吸着性能は、上記脱離スペクトルか
ら以下のように評価することができる。HC吸着容量
は、脱離スペクトルを積分して得られるHC脱離量から
見積もることができ、吸着保持力は、脱離ピーク温度及
び/または所定温度以上での脱離量で見積もることがで
きる。表2に、吸着剤重量当たりの200℃以上でのト
ルエン脱離量(μmol/g)、及び脱離ピーク温度
(℃)を示す。The adsorption performance of HC can be evaluated from the above desorption spectrum as follows. The HC adsorption capacity can be estimated from the HC desorption amount obtained by integrating the desorption spectrum, and the adsorption retention power can be estimated from the desorption peak temperature and / or the desorption amount at a predetermined temperature or higher. Table 2 shows the amount of desorbed toluene (μmol / g) at 200 ° C. or more per adsorbent weight and the desorption peak temperature (° C.).
【0041】[0041]
【表1】 [Table 1]
【0042】<吸着剤の耐久試験>吸着剤1〜5及び比
較吸着剤1〜12を各々加圧成形後、粉砕して12〜2
0メッシュに整粒した。整粒した吸着剤に、Airガス
にH2Oを10体積%となるように含有させた混合ガス
(耐久−A:酸化雰囲気)あるいは窒素にプロピレン
(5000ppmC)とH2O(10体積%)を含有さ
せた混合ガス(耐久―B:還元雰囲気)を流通しなが
ら、850℃で5時間処理した。これら耐久処理を施し
た吸着剤を<HC吸着除去試験>と同様な前処理、評価
条件でHC吸着性能を評価した。耐久後の、吸着剤重量
当たりの200℃以上でのトルエン脱離量(μmol/
g)及び脱離ピーク温度(℃)を表2に示す。<Durability test of adsorbent> Adsorbents 1 to 5 and comparative adsorbents 1 to 12 were each molded under pressure and then pulverized to 12 to 2
It was sized to 0 mesh. The granulated adsorbent, mixed gas containing of H 2 O in Air gas such that 10% by volume: and H 2 O (10 vol%) propylene (5000PpmC) to (durable -A oxidizing atmosphere) or nitrogen Was processed at 850 ° C. for 5 hours while flowing a mixed gas containing (A-B: reducing atmosphere). The adsorbents subjected to these durability treatments were evaluated for HC adsorption performance under the same pretreatment and evaluation conditions as in the <HC adsorption removal test>. After endurance, the amount of desorbed toluene at 200 ° C or more per adsorbent weight (μmol /
g) and desorption peak temperature (° C.) are shown in Table 2.
【0043】[0043]
【表2】 [Table 2]
【0044】[0044]
【発明の効果】本発明のHC吸着剤は、吸着したHCの
高温での脱離量が多く、その脱離温度が高いというHC
吸着性能を有する。更には酸化雰囲気下及び還元雰囲気
下での耐久処理後でも、高いHC吸着性能を維持し、吸
着剤がいかなる雰囲気で高温に晒された後でも優れたH
C吸着特性を示す。従って、本発明の吸着剤を、HCを
含有する処理ガスに接触させることで、従来技術で開示
されている吸着剤よりも排ガス中のHCを効率良く吸着
除去できる。また、本発明の吸着剤は、排ガス浄化触媒
と組み合わせて、吸着HCを利用した窒素酸化物の除去
に適用することも可能である。The HC adsorbent of the present invention has a large amount of adsorbed HC desorbed at a high temperature and has a high desorbing temperature.
Has adsorption performance. Furthermore, even after endurance treatment in an oxidizing atmosphere and a reducing atmosphere, high HC adsorption performance is maintained, and even when the adsorbent is exposed to high temperatures in any atmosphere, excellent H is obtained.
Shows C adsorption characteristics. Therefore, by bringing the adsorbent of the present invention into contact with the treatment gas containing HC, HC in the exhaust gas can be adsorbed and removed more efficiently than the adsorbent disclosed in the related art. Further, the adsorbent of the present invention can be applied to removal of nitrogen oxides using adsorbed HC in combination with an exhaust gas purifying catalyst.
───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 3G091 AA02 AA17 AA18 AB04 AB10 BA14 BA15 BA39 FA14 FB03 FB10 FB12 FC08 GB02Y GB09Y HA18 4D002 AA33 AA34 AB03 AC10 BA04 CA07 DA01 DA45 EA06 GA01 GB08 4G066 AA13B AA62B AA62C BA38 CA04 CA51 DA02 FA12 FA22 FA34 FA37 ──────────────────────────────────────────────────続 き Continued on the front page F-term (reference) FA22 FA34 FA37
Claims (8)
及び遷移金属を含有しないゼオライトからなることを特
徴とする、炭化水素吸着剤。1. A hydrocarbon adsorbent comprising a zeolite containing an alkali metal and not containing an alkaline earth metal and a transition metal.
ばれる少なくとも一種であることを特徴とする、請求項
1に記載の炭化水素吸着剤。2. The hydrocarbon adsorbent according to claim 1, wherein the alkali metal is at least one selected from the group consisting of K, Rb and Cs.
る、請求項1または2に記載の炭化水素吸着剤。3. The hydrocarbon adsorbent according to claim 1, wherein the alkali metal is Cs.
少なくとも10であることを特徴とする、請求項1〜3
いずれかに記載の炭化水素吸着剤。4. The zeolite according to claim 1, wherein the molar ratio of SiO 2 / Al 2 O 3 is at least 10.
The hydrocarbon adsorbent according to any one of the above.
ることを特徴とする、請求項1〜4いずれかに記載の炭
化水素吸着剤。5. The hydrocarbon adsorbent according to claim 1, wherein the alkali metal is contained by ion exchange.
て0.1〜30重量%であることを特徴とする、請求項
1〜5いずれかに記載の炭化水素吸着剤。6. The hydrocarbon adsorbent according to claim 1, wherein the content of the alkali metal is 0.1 to 30% by weight based on the zeolite.
EA、FAUの群から選ばれる一種以上であることを特
徴とする、請求項1〜6いずれかに記載の炭化水素吸着
剤。7. The method according to claim 1, wherein the zeolite is FER, MFI, MOR, B
The hydrocarbon adsorbent according to any one of claims 1 to 6, wherein the hydrocarbon adsorbent is at least one member selected from the group consisting of EA and FAU.
着剤を処理ガスに接触させることを特徴とする、炭化水
素の吸着除去方法。8. A method for adsorbing and removing hydrocarbons, comprising bringing the hydrocarbon adsorbent according to claim 1 into contact with a processing gas.
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| KR20160082777A (en) * | 2014-12-29 | 2016-07-11 | 현대자동차주식회사 | An oxidation-reduction catalyst desorbing hydrocarbon at high temperature and a device for eliminating exhast gas comprising the catalyst |
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