JPH06198131A - Material for removing nitrogen oxide and method for removing nitrogen oxide - Google Patents
Material for removing nitrogen oxide and method for removing nitrogen oxideInfo
- Publication number
- JPH06198131A JPH06198131A JP4360039A JP36003992A JPH06198131A JP H06198131 A JPH06198131 A JP H06198131A JP 4360039 A JP4360039 A JP 4360039A JP 36003992 A JP36003992 A JP 36003992A JP H06198131 A JPH06198131 A JP H06198131A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- silver
- nitrogen
- oxygen
- oxide
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
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- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は窒素酸化物と過剰の酸素
を含む燃焼排ガスから、窒素酸化物を効果的に除去する
ことのできる除去材及びそれを用いた窒素酸化物除去方
法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a scavenger capable of effectively removing nitrogen oxides from a combustion exhaust gas containing nitrogen oxides and excess oxygen, and a nitrogen oxides removing method using the same.
【0002】[0002]
【従来の技術及び発明が解決しようとする課題】自動車
用エンジン等の内燃機関や、工場等に設置された燃焼機
器、家庭用ファンヒーターなどから排出される各種の燃
焼排ガス中には、過剰の酸素とともに一酸化窒素、二酸
化窒素等の窒素酸化物が含まれている。ここで、「過剰
の酸素を含む」とは、その排ガス中に含まれる一酸化炭
素、水素、炭化水素等の未燃焼成分を燃焼するのに必要
な理論酸素量より多い酸素を含むことを意味する。ま
た、以下における窒素酸化物とは一酸化窒素及び/又は
二酸化窒素を指す。2. Description of the Related Art Excessive amounts of combustion exhaust gas discharged from internal combustion engines such as automobile engines, combustion equipment installed in factories, household fan heaters, etc. Nitrogen oxides such as nitric oxide and nitrogen dioxide are contained together with oxygen. Here, "containing excess oxygen" means containing more oxygen than the theoretical oxygen amount necessary to burn unburned components such as carbon monoxide, hydrogen, and hydrocarbons contained in the exhaust gas. To do. Moreover, the nitrogen oxide in the following refers to nitric oxide and / or nitrogen dioxide.
【0003】この窒素酸化物は酸性雨の原因の一つとさ
れ、環境上の大きな問題となっている。そのため、各種
燃焼機器が排出する排ガス中の窒素酸化物を除去するさ
まざまな方法が検討されている。This nitrogen oxide is considered to be one of the causes of acid rain and is a serious environmental problem. Therefore, various methods for removing nitrogen oxides in exhaust gas discharged from various combustion devices have been studied.
【0004】過剰の酸素を含む燃焼排ガスから窒素酸化
物を除去する方法として、特に大規模な固定燃焼装置
(工場等の大型燃焼機等)に対しては、アンモニアを用
いる選択的接触還元法が実用化されている。As a method for removing nitrogen oxides from combustion exhaust gas containing excess oxygen, a selective catalytic reduction method using ammonia is used, particularly for large-scale fixed combustion devices (large combustors such as factories). It has been put to practical use.
【0005】しかしながら、この方法においては、窒素
酸化物の還元剤として用いるアンモニアが高価であるこ
と、またアンモニアは毒性を有すること、そのために未
反応のアンモニアが排出しないように排ガス中の窒素酸
化物濃度を計測しながらアンモニア注入量を制御しなけ
ればならないこと、一般に装置が大型となること等の問
題点がある。However, in this method, ammonia used as a reducing agent for nitrogen oxides is expensive, and ammonia is toxic, so that unreacted ammonia is discharged so that nitrogen oxides in exhaust gas are not discharged. There are problems that the amount of ammonia injection must be controlled while measuring the concentration and that the apparatus is generally large.
【0006】そこで、ゼオライト又はそれに遷移金属を
担持した触媒を用いて、排ガス中の酸素との理論反応量
以下の還元剤を添加して窒素酸化物を除去する方法が提
案された(たとえば、特開昭63-100919 号、同63-28372
7 号、特開平1-130735号、及び日本化学会第59春季年会
(1990年)2A526、同第60秋季年会 (1990年)3L420、3L42
2 、3L423 、「触媒」vol.33 No.2 、59ページ、1991年
等) 。又、銀を担持する触媒を用いる方法が提案された
(特開平4-281844)。Therefore, there has been proposed a method for removing nitrogen oxides by adding a reducing agent in an amount equal to or less than a theoretical reaction amount with oxygen in exhaust gas by using zeolite or a catalyst supporting a transition metal thereon (for example, a special method). Kaisho 63-100919, 63-28372
No. 7, JP-A-1-130735, and 59th Annual Meeting of the Chemical Society of Japan
(1990) 2A526, 60th Autumn Meeting (1990) 3L420, 3L42
2, 3L423, "Catalyst" vol.33 No.2, page 59, 1991 etc.). In addition, a method using a catalyst supporting silver has been proposed (JP-A-4-218844).
【0007】しかしながら、これらの方法では、水分を
含まないような模擬排ガスに対しては高い効率で窒素酸
化物を除去することはできるが、実際の排ガスでは水分
を10%程度含有するので、窒素酸化物の除去率が著し
く低下することがわかった。また、これらの方法では、
窒素酸化物の還元反応の最適温度が400 〜600 ℃程度と
高くなる不都合もある。また、銀又は酸化銀を担持した
触媒では、光に当たると触媒活性が低下し、窒素酸化物
の除去率が低下する欠点がある。However, although these methods can remove nitrogen oxides with high efficiency from simulated exhaust gas that does not contain water, the actual exhaust gas contains about 10% of water, so It was found that the oxide removal rate was significantly reduced. Also, with these methods,
There is also the disadvantage that the optimum temperature for the reduction reaction of nitrogen oxides is as high as 400 to 600 ° C. Further, a catalyst supporting silver or silver oxide has a drawback that the catalytic activity is lowered when exposed to light and the removal rate of nitrogen oxides is lowered.
【0008】したがって、本発明の目的は、固定燃焼装
置および酸素過剰条件で燃焼するガソリンエンジン、デ
ィーゼルエンジン等からの燃焼排ガスのように、窒素酸
化物や、一酸化炭素、水素、炭化水素等の未燃焼分に対
する理論反応量以上の酸素を含有する燃焼排ガスから、
低温のときでも効果的に窒素酸化物を除去することがで
きる窒素酸化物除去材、及び除去方法を提供することで
ある。Therefore, an object of the present invention is to remove nitrogen oxides, carbon monoxide, hydrogen, hydrocarbons, etc., such as combustion exhaust gas from a fixed combustion apparatus and a gasoline engine, a diesel engine, etc. that burn under an excess oxygen condition. From the combustion exhaust gas that contains more than the theoretical reaction amount of oxygen for unburned components,
It is intended to provide a nitrogen oxide removing material and a removing method capable of effectively removing nitrogen oxide even at a low temperature.
【0009】[0009]
【課題を解決するための手段】上記課題に鑑み鋭意研究
の結果、本発明者は、多孔質の無機酸化物に特定量の硫
酸銀を担持してなる除去材を用い、この除去材に特定の
温度及び接触時間で排ガスを接触させて、排ガスに含ま
れる窒素酸化物の量に見合うように排ガス中に添加され
た炭化水素又は含酸素有機化合物により、水分を10%
程度含有する排ガスでも、窒素酸化物を効果的に除去す
ることができる上、低温領域における窒素酸化物の除去
性能が向上することを発見し、本発明を完成した。As a result of earnest research in view of the above problems, the present inventor has used a removing material in which a specific amount of silver sulfate is supported on a porous inorganic oxide, and is specified as the removing material. The exhaust gas is brought into contact with the exhaust gas at the temperature and contact time of 10%, and the water content is 10% by the hydrocarbon or oxygen-containing organic compound added to the exhaust gas so as to correspond to the amount of nitrogen oxides contained in the exhaust gas.
The present invention was completed by discovering that nitrogen oxides can be effectively removed even with exhaust gas containing a small amount thereof, and that the nitrogen oxide removal performance in a low temperature region is improved.
【0010】すなわち、窒素酸化物と、共存する未燃焼
成分に対する理論反応量より多い酸素とを含む燃焼排ガ
スから窒素酸化物を除去する本発明の窒素酸化物除去材
は、多孔質の無機酸化物に硫酸銀を銀元素に換算して
0.2〜15重量%、又は0.2〜15重量%の銀と銀
のモル数の1/50〜2倍の硫酸とを担持してなり、外
部から前記排ガス中に添加された炭化水素又は含酸素有
機化合物を還元剤として、200〜600℃で、前記排
ガス中の窒素酸化物を還元することを特徴とする。That is, the nitrogen oxide removing material of the present invention for removing nitrogen oxides from a combustion exhaust gas containing nitrogen oxides and oxygen in an amount larger than the theoretical reaction amount for coexisting unburned components is a porous inorganic oxide. In addition, 0.2 to 15% by weight or 0.2 to 15% by weight of silver sulfate converted to elemental silver and sulfuric acid of 1/50 to 2 times the number of moles of silver are supported. From the hydrocarbon or oxygen-containing organic compound added to the exhaust gas as a reducing agent at 200 to 600 ° C. to reduce nitrogen oxides in the exhaust gas.
【0011】また、窒素酸化物と、共存する未燃焼成分
に対する理論反応量より多い酸素とを含む燃焼排ガスか
ら窒素酸化物を除去する本発明の窒素酸化物除去方法
は、上記窒素酸化物除去材を排ガス導管の途中に設置
し、前記除去材の上流側で前記排ガス中に炭化水素又は
含酸素有機化合物を添加し、200〜600℃で前記排
ガスを前記除去材に接触させ、前記炭化水素又は含酸素
有機化合物と前記窒素酸化物とを反応させて前記窒素酸
化物を除去することを特徴とする。Further, the nitrogen oxide removing method of the present invention for removing nitrogen oxides from a combustion exhaust gas containing nitrogen oxides and oxygen in an amount larger than the theoretical reaction amount for coexisting unburned components is the above-mentioned nitrogen oxide removing material. Is installed in the middle of the exhaust gas conduit, a hydrocarbon or an oxygen-containing organic compound is added to the exhaust gas on the upstream side of the removing material, and the exhaust gas is brought into contact with the removing material at 200 to 600 ° C. It is characterized in that the oxygen-containing organic compound is reacted with the nitrogen oxide to remove the nitrogen oxide.
【0012】以下、本発明を詳細に説明する。本発明で
は、以下に示す除去材を用い、この除去材に排ガスを接
触させることにより、排ガス中の残留炭化水素及び/又
は除去材の設置部位より上流側で排ガスに添加された炭
化水素又は含酸素有機化合物を還元剤として排ガス中の
窒素酸化物を還元除去する。The present invention will be described in detail below. In the present invention, a removing material shown below is used, and exhaust gas is brought into contact with this removing material to remove residual hydrocarbons in the exhaust gas and / or hydrocarbons added to the exhaust gas on the upstream side from the installation site of the removing material or the content of the hydrocarbon. Nitrogen oxides in exhaust gas are reduced and removed using an oxygen organic compound as a reducing agent.
【0013】まず、本発明の除去材は多孔質の無機酸化
物に硫酸銀、又は銀と硫酸を担持してなる。多孔質の無
機酸化物としては、多孔質のアルミナ、チタニア、ジル
コニア、及びそれらの複合酸化物等を使用することがで
きるが、好ましくはγ−アルミナ又はアルミナ系複合酸
化物を用いる。γ−アルミナ又はアルミナ系複合酸化物
を用いることにより、添加した炭化水素又は含酸素有機
化合物と排ガス中の窒素酸化物との反応が効率良く起こ
る。First, the removing material of the present invention comprises silver sulfate or silver and sulfuric acid supported on a porous inorganic oxide. As the porous inorganic oxide, porous alumina, titania, zirconia, and their composite oxides can be used, but γ-alumina or alumina-based composite oxide is preferably used. By using γ-alumina or an alumina-based composite oxide, the reaction between the added hydrocarbon or oxygen-containing organic compound and the nitrogen oxide in the exhaust gas occurs efficiently.
【0014】多孔質の無機酸化物の比表面積は10m2
/g以上であるのが好ましい。比表面積が10m2 /g
未満であると、無機酸化物への銀成分(銀活性種)の分
散が悪くなり、良好な窒素酸化物の除去が行えない。好
ましい多孔質無機酸化物の比表面積は30m2 /g以上
とする。The specific surface area of the porous inorganic oxide is 10 m 2
/ G or more is preferable. Specific surface area of 10 m 2 / g
If it is less than the above range, the dispersion of the silver component (silver active species) in the inorganic oxide becomes poor, and the nitrogen oxide cannot be removed well. The specific surface area of the porous inorganic oxide is preferably 30 m 2 / g or more.
【0015】本発明の除去材はペレット状、粉末状、ハ
ニカム状、フォーム状、板状等の形態で用いることがで
きる。本発明の除去材の好ましい形態は多孔質無機酸化
物に硫酸銀、又は銀と硫酸を担持した触媒を、セラミッ
ク製又は金属製ハニカム状、発泡状等の三次元構造体の
表面にコートするか、上記三次元構造体に無機酸化物を
コートしたあと、硫酸銀、又は銀と硫酸を担持して調製
する。セラミック材として耐熱性の優れたコージェライ
ト、ムライトなどが挙げられる。三次元構造体への無機
酸化物のコートは公知のウォッシュコート法などにより
行なう。本発明の除去材のもう一つの好ましい形態はペ
レット状の多孔質無機酸化物に硫酸銀、又は銀と硫酸を
担持して用いる。The removing material of the present invention can be used in the form of pellets, powder, honeycomb, foam, plate or the like. The preferred form of the removing material of the present invention is to coat the surface of a three-dimensional structure such as a ceramic or metal honeycomb-like or foam-like one with a catalyst in which silver sulfate or silver and sulfuric acid is supported on a porous inorganic oxide. After coating the above-mentioned three-dimensional structure with an inorganic oxide, silver sulfate or silver and sulfuric acid is carried to prepare. Examples of the ceramic material include cordierite and mullite, which have excellent heat resistance. The inorganic oxide is coated on the three-dimensional structure by a known wash coating method or the like. Another preferred form of the removing material of the present invention is a pellet-shaped porous inorganic oxide loaded with silver sulfate or silver and sulfuric acid.
【0016】上記したγ−アルミナ等の無機酸化物に硫
酸銀を担持する場合の担持量は、無機酸化物を100重
量%として、その0.2〜15重量%(銀元素換算値)
とする。硫酸銀成分が0.2重量%(銀元素換算値)未
満では低温側での窒素酸化物の除去率が低下する。ま
た、15重量%(銀元素換算値)を超す量の銀を担持す
ると炭化水素自身の燃焼が起きやすく、窒素酸化物の除
去率はかえって低下する。好ましくは、銀の担持量を無
機酸化物100重量%に対して、5重量%を越えて15
重量%以下(銀元素換算値)とする。銀又は銀酸化物を
担持した除去材は、低温領域において窒素酸化物の除去
活性が低下するのに対して、硫酸銀が担持された除去材
は低温領域でも高い除去活性が維持される。The amount of silver sulfate supported on the above-mentioned inorganic oxide such as γ-alumina is 0.2 to 15% by weight (in terms of silver element) with 100% by weight of the inorganic oxide.
And When the content of silver sulfate is less than 0.2% by weight (converted to silver element), the removal rate of nitrogen oxides on the low temperature side decreases. Further, when the amount of silver that exceeds 15% by weight (converted to silver element) is carried, the hydrocarbon itself is easily burned, and the nitrogen oxide removal rate is rather lowered. Preferably, the supported amount of silver exceeds 15% by weight with respect to 100% by weight of the inorganic oxide.
Weight% or less (converted to silver element). The removing material supporting silver or silver oxide has a low nitrogen oxide removing activity in a low temperature region, whereas the removing material supporting silver sulfate maintains a high removing activity even in a low temperature region.
【0017】さらに、上記したγ−アルミナ等の無機酸
化物に銀と硫酸を担持する場合、銀成分の担持量は、無
機酸化物を100重量%として、その0.2〜15重量
%(銀元素換算値)とする。銀成分が0.2重量%(銀
元素換算値)未満では低温側での窒素酸化物の除去率が
低下する。また、15重量%(銀元素換算値)を超す量
の銀を担持すると炭化水素自身の燃焼が起きやすく、窒
素酸化物の除去率はかえって低下する。好ましくは、銀
の担持量を無機酸化物100重量%に対して、5重量%
を越えて15重量%以下(銀元素換算値)とする。銀又
は銀酸化物を担持した除去材は、低温領域において窒素
酸化物の除去活性が低下するのに対して、銀と硫酸が担
持された除去材は低温領域でも高い除去活性が維持され
る。硫酸の担持量が銀の担持量と等モル数でなくでもよ
い。硫酸の担持量を銀の担持量の1/50〜2倍(モル
比)とするのが好ましい。Furthermore, when silver and sulfuric acid are supported on the above-mentioned inorganic oxide such as γ-alumina, the amount of the silver component supported is 0.2 to 15% by weight (silver) with 100% by weight of the inorganic oxide. Element conversion value). If the silver component is less than 0.2% by weight (converted to silver element), the nitrogen oxide removal rate on the low temperature side is lowered. Further, when the amount of silver that exceeds 15% by weight (converted to silver element) is carried, the hydrocarbon itself is easily burned, and the nitrogen oxide removal rate is rather lowered. Preferably, the supported amount of silver is 5% by weight with respect to 100% by weight of the inorganic oxide.
To 15% by weight or less (silver element conversion value). The removing material supporting silver or silver oxide has a low nitrogen oxide removing activity in a low temperature region, whereas the removing material supporting silver and sulfuric acid maintains a high removing activity even in a low temperature region. The amount of sulfuric acid carried need not be the same number of moles as the amount of silver carried. The amount of sulfuric acid carried is preferably 1/50 to 2 times (molar ratio) the amount of silver carried.
【0018】γ−アルミナ等の無機酸化物に硫酸銀など
を担持する方法としては、公知の含浸法や、混練法等を
用いることができる。担持後の除去材の調整は、50〜
150℃程度で乾燥後、100〜600℃で段階的に昇
温して焼成するのが好ましい。焼成は、空気中又は窒素
流通下、あるいは水素ガス流通下、もしくは真空排気し
ながら行うのが好ましい。なお、窒素ガスまたは水素ガ
ス流通下で焼成した除去材は、最後に酸化処理を行うこ
とが好ましい。As a method for supporting silver sulfate or the like on an inorganic oxide such as γ-alumina, a known impregnation method, a kneading method or the like can be used. Adjustment of the removal material after loading is 50-
It is preferable that after drying at about 150 ° C., the temperature is raised stepwise at 100 to 600 ° C. for firing. The firing is preferably performed in air or under nitrogen flow, or under hydrogen gas flow, or while evacuating. It is preferable that the removal material fired under the flow of nitrogen gas or hydrogen gas is finally subjected to an oxidation treatment.
【0019】次に、本発明の方法について説明する。ま
ず、上述した除去材を排ガス導管の途中に設置する。Next, the method of the present invention will be described. First, the above-mentioned removal material is installed in the middle of the exhaust gas conduit.
【0020】排ガス中には、残留炭化水素としてアセチ
レン、メタン、エタン、プロピレン等が含まれるが、排
ガス中のNOx を還元するのに十分な量の残留炭化水素が
含まれていない場合には、外部から炭化水素又は含酸素
有機化合物を排ガス中に導入する。炭化水素又は含酸素
有機化合物の導入位置は、除去材を設置した位置より上
流側である。The exhaust gas contains acetylene, methane, ethane, propylene and the like as residual hydrocarbons, but when the residual hydrocarbons are not contained in an amount sufficient to reduce NOx in the exhaust gas, A hydrocarbon or an oxygen-containing organic compound is introduced into the exhaust gas from the outside. The introduction position of the hydrocarbon or the oxygen-containing organic compound is upstream of the position where the removing material is installed.
【0021】外部から導入する炭化水素としては、プロ
ピレン、アセチレン、プロパン等の標準状態でガス状の
炭化水素の他に、標準状態で液体状の炭化水素も用いる
ことができる。標準状態で液体状の炭化水素としては、
具体的には、軽油、セタン、ヘプタン、灯油等が挙げら
れる。含酸素有機化合物として、エタノール等のアルコ
ール類が好ましい。これらの添加物は、噴霧等の方法で
排ガス中に導入することができる。As the hydrocarbon introduced from the outside, in addition to the gaseous hydrocarbon in the standard state such as propylene, acetylene, propane, etc., a hydrocarbon in the liquid state in the standard state can be used. As a liquid hydrocarbon in the standard state,
Specific examples include light oil, cetane, heptane, and kerosene. As the oxygen-containing organic compound, alcohols such as ethanol are preferable. These additives can be introduced into the exhaust gas by a method such as spraying.
【0022】外部から導入する炭化水素又は含酸素有機
化合物の量は、排ガス中の窒素酸化物の重量の5倍以下
とするのが好ましい。添加量が5倍を超えると、燃費の
悪化を招く。より好ましくは0.2〜4倍とする。The amount of hydrocarbon or oxygen-containing organic compound introduced from the outside is preferably not more than 5 times the weight of nitrogen oxide in the exhaust gas. If the addition amount exceeds 5 times, the fuel efficiency is deteriorated. It is more preferably 0.2 to 4 times.
【0023】本発明では、炭化水素または含酸素有機化
合物を含む排ガスが上記した除去材と接触する時間を調
節し、添加物と窒素酸化物との反応を効率良く進行させ
る。実用的な立場で考えて、炭化水素又は含酸素有機化
合物を含む排ガスと除去材との接触時間は0.006g
・秒/ml以上とする。好ましい接触時間は0.007g
・秒/ml以上とする。In the present invention, the time during which the exhaust gas containing the hydrocarbon or the oxygen-containing organic compound is in contact with the above-mentioned removing material is adjusted so that the reaction between the additive and the nitrogen oxides proceeds efficiently. From a practical standpoint, the contact time between the exhaust gas containing hydrocarbons or oxygen-containing organic compounds and the removal material is 0.006 g.
・ Seconds / ml or more. Preferred contact time is 0.007g
・ Seconds / ml or more.
【0024】また、本発明では、炭化水素又は含酸素有
機化合物と窒素酸化物とが反応する部位である除去材設
置部位における排ガスの温度を200〜600℃に保
つ。排ガスの温度が200℃未満であると窒素酸化物の
還元反応が進行せず、良好な窒素酸化物の除去を行うこ
とができない。一方、600℃を超す温度とすると炭化
水素又は含酸素有機化合物自身の燃焼が始まり、窒素酸
化物の還元除去が行えない。好ましい排ガス温度は30
0〜550℃とする。Further, in the present invention, the temperature of the exhaust gas at the site where the removing material is installed, which is the site where the hydrocarbon or the oxygen-containing organic compound reacts with the nitrogen oxide, is maintained at 200 to 600 ° C. If the temperature of the exhaust gas is less than 200 ° C., the reduction reaction of nitrogen oxides does not proceed, and good removal of nitrogen oxides cannot be performed. On the other hand, if the temperature exceeds 600 ° C., the combustion of the hydrocarbon or the oxygen-containing organic compound itself starts, and the nitrogen oxide cannot be reduced and removed. Preferred exhaust gas temperature is 30
The temperature is 0 to 550 ° C.
【0025】[0025]
【実施例】本発明を以下の具体的実施例によりさらに詳
細に説明する。実施例1 市販のγ−アルミナ成形体(直径1.5mm 、長さ約6mm、
比表面積260m2 /g)10gを硫酸銀水溶液(2.
5Mの硝酸20mlに硫酸銀0.61gを溶かした溶
液)に20分間浸漬したあと、空気中、80℃で2時間
した。次に、酸素10%を含む窒素気流下、毎分2.5
℃で550℃まで昇温したあと、550℃で5時間焼成
し、γ−アルミナ成形体に対して2.0重量%(元素換
算値)の銀を硫酸銀の形で担持した。The present invention will be described in more detail by the following specific examples. Example 1 Commercially available γ-alumina molded body (diameter 1.5 mm, length about 6 mm,
10 g of a specific surface area of 260 m 2 / g) was added to an aqueous solution of silver sulfate (2.
It was immersed in a solution of 0.61 g of silver sulfate in 20 ml of 5 M nitric acid) for 20 minutes, and then in air at 80 ° C. for 2 hours. Next, under a nitrogen stream containing 10% oxygen, 2.5 per minute
After the temperature was raised to 550 ° C. at 5 ° C., it was baked at 550 ° C. for 5 hours, and 2.0% by weight (elemental conversion value) of silver was supported in the form of silver sulfate on the γ-alumina formed body.
【0026】実施例2 市販のγ−アルミナ成形体(直径1.5mm 、長さ約6mm、
比表面積260m2 /g)10gを97mMの硫酸水溶
液20mlに20分間浸漬したあと、空気中、80℃で
2時間乾燥した。次に、酸素10%を含む窒素気流下、
毎分2.5℃で550℃まで昇温したあと、550℃で
5時間焼成し、室温まで冷却した。そして、上記γ−ア
ルミナを硝酸銀溶液(水20mlに硝酸銀0.67gを
溶かした溶液)に20分間浸漬したあと、空気中、80
℃で2時間乾燥し、酸素10%を含む窒素気流下、毎分
2.5℃で550℃まで昇温し、550℃で5時間焼成
し、γ−アルミナ成形体に対して2重量%(元素換算
値)の銀と0.09重量%の硫酸を担持した。 Example 2 Commercially available γ-alumina molded body (diameter 1.5 mm, length about 6 mm,
10 g of a specific surface area of 260 m 2 / g) was immersed in 20 ml of a 97 mM aqueous sulfuric acid solution for 20 minutes, and then dried in air at 80 ° C. for 2 hours. Next, under a nitrogen stream containing 10% oxygen,
After heating to 550 ° C. at 2.5 ° C./min, firing was performed at 550 ° C. for 5 hours and cooling to room temperature. Then, the above γ-alumina was immersed in a silver nitrate solution (solution in which 0.67 g of silver nitrate was dissolved in 20 ml of water) for 20 minutes, and then, in air, at 80
After drying at ℃ for 2 hours, under a nitrogen stream containing 10% oxygen, the temperature was raised to 550 ℃ at 2.5 ℃ / min, and baked at 550 ℃ for 5 hours, 2 wt% ( Silver (elemental conversion value) and 0.09% by weight of sulfuric acid were supported.
【0027】実施例3 市販のγ−アルミナ成形体(直径1.5mm 、長さ約6mm、
比表面積260m2 /g)10gを硝酸銀溶液(水20
mlに硝酸銀0.67gを溶かした溶液)に20分間浸
漬したあと、空気中、80℃で2時間乾燥した。次に、
酸素10%を含む窒素気流下、毎分2.5℃で550℃
まで昇温したあと、550℃で5時間焼成し、室温まで
冷却した。そして、上記γ−アルミナを97mMの硫酸
水溶液20mlに20分間浸漬したあと、空気中、80
℃で2時間乾燥し、酸素10%を含む窒素気流下、毎分
2.5℃で550℃まで昇温し、550℃で5時間焼成
し、γ−アルミナ成形体に対して2重量%(元素換算
値)の銀と0.09重量%の硫酸を担持した。 Example 3 Commercially available γ-alumina molded body (diameter 1.5 mm, length about 6 mm,
10 g of specific surface area 260 m 2 / g) in silver nitrate solution (water 20
It was immersed in a solution of 0.67 g of silver nitrate in 20 ml) for 20 minutes and then dried in air at 80 ° C. for 2 hours. next,
550 ° C at 2.5 ° C / min under nitrogen stream containing 10% oxygen
After heating to 50 ° C., the mixture was baked at 550 ° C. for 5 hours and cooled to room temperature. Then, the above γ-alumina was immersed in 20 ml of 97 mM sulfuric acid aqueous solution for 20 minutes, and then, in air,
After drying at ℃ for 2 hours, under nitrogen stream containing 10% oxygen, the temperature was raised to 550 ℃ at 2.5 ℃ per minute, and baked at 550 ℃ for 5 hours, and 2 wt% ( Silver (elemental conversion value) and 0.09% by weight of sulfuric acid were supported.
【0028】実施例4〜6 実施例1〜3で作成した除去材を、反応管内に設置し、
表1に示す組成のガス(一酸化窒素、二酸化炭素、酸
素、プロピレン、及び窒素からなる乾燥成分の合計10
0容量%に、さらに水分10容量%を添加したもの)を
用いて、毎分2リットル(標準状態)の流量で流して
(接触時間0.3g・秒/ml、空間速度6400hr
-1)、反応管の排ガス温度を300〜550℃の範囲に
保ち、プロピレンと窒素酸化物とを反応させて、窒素酸
化物の除去率を求めた。結果を表2に示す。 Examples 4 to 6 The removing materials prepared in Examples 1 to 3 were placed in a reaction tube,
A gas having the composition shown in Table 1 (a total of 10 dry components consisting of nitric oxide, carbon dioxide, oxygen, propylene, and nitrogen).
Using 0% by volume and 10% by volume of water added), the mixture was allowed to flow at a flow rate of 2 liters per minute (standard state) (contact time: 0.3 g · sec / ml, space velocity: 6400 hr).
-1 ), the exhaust gas temperature of the reaction tube was kept in the range of 300 to 550 ° C., propylene was reacted with nitrogen oxide, and the nitrogen oxide removal rate was obtained. The results are shown in Table 2.
【0029】反応管通過後のガスの窒素酸化物(一酸化
窒素、二酸化窒素の合計量)の濃度を化学発光式窒素酸
化物分析計により測定し、窒素酸化物の除去率を求め
た。結果を表2に示す。The concentration of nitrogen oxides (total amount of nitric oxide and nitrogen dioxide) of the gas after passing through the reaction tube was measured by a chemiluminescence type nitrogen oxide analyzer to determine the removal rate of nitrogen oxides. The results are shown in Table 2.
【0030】 表1 成分 濃度 一酸化窒素 500 ppm 二酸化炭素 10 容量% 酸素 10 容量% プロピレン 500 ppm 窒素 残部 水分 上記した成分からなるガス量に対して10容量%Table 1 Component Concentration Nitric oxide 500 ppm Carbon dioxide 10% by volume Oxygen 10% by volume Propylene 500 ppm Nitrogen balance Moisture 10% by volume based on the amount of gas composed of the above components
【0031】比較例1 実施例1で用いたγ−アルミナペレットと同一のものに
硝酸銀水溶液を用いて硝酸銀を2.0重量%(銀元素換
算)担持して、乾燥、600℃まで焼成により調製した
除去材を用い、他は実施例4と同様な条件で窒素酸化物
の除去試験を行った。結果を表2に示す。 Comparative Example 1 Prepared by carrying out 2.0% by weight (in terms of silver element) of silver nitrate on the same γ-alumina pellets as used in Example 1 using an aqueous solution of silver nitrate, drying and baking to 600 ° C. A nitrogen oxide removal test was conducted under the same conditions as in Example 4 except that the above removing material was used. The results are shown in Table 2.
【0032】 表2 窒素酸化物の除去率(%) 温度(℃) 実施例4 実施例5 実施例6 比較例1 300 11.8 11.0 10.5 0.0 350 33.9 30.5 28.0 2.0 400 59.5 45.8 40.5 17.2 450 67.8 60.5 63.3 57.3 500 57.7 56.7 60.5 56.7 550 22.9 30.2 27.6 37.8 Table 2 Nitrogen oxide removal rate (%) Temperature (° C.) Example 4 Example 5 Example 6 Comparative Example 1 300 11.8 11.0 10.5 0.0 350 33.9 30.5 28.0 2.0 400 59.5 45.8 40.5 17.2 450 67.8 60.5 63.3 57.3 500 57.7 56.7 60.5 56.7 550 22.9 30 .2 27.6 37.8
【0033】表2からわかるように、実施例では、40
0℃以下でも窒素酸化物の除去が見られた。一方、比較
例1では、低温側で窒素酸化物除去率の低下がみられ
た。As can be seen from Table 2, in the embodiment, 40
Removal of nitrogen oxide was observed even at 0 ° C or lower. On the other hand, in Comparative Example 1, the nitrogen oxide removal rate decreased at the low temperature side.
【0034】[0034]
【発明の効果】以上詳述したように、本発明の方法によ
れば、過剰の酸素を含む排ガス中の窒素酸化物を効率良
く除去することができる。また、本発明の方法では、排
ガス中に水分が10%程度含まれている場合でも窒素酸
化物の除去を効率良く行うことができる。As described in detail above, according to the method of the present invention, nitrogen oxides in exhaust gas containing excess oxygen can be efficiently removed. Further, according to the method of the present invention, nitrogen oxides can be efficiently removed even when the exhaust gas contains about 10% of water.
【0035】本発明の窒素酸化物除去方法は、各種燃焼
機、自動車等の排ガスに含まれる窒素酸化物の除去に広
く利用することができる。The method for removing nitrogen oxides of the present invention can be widely used for removing nitrogen oxides contained in exhaust gas from various combustors, automobiles and the like.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 吉田 清英 埼玉県熊谷市末広四丁目14番1号 株式会 社リケン熊谷事業所内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Kiyohide Yoshida 4-1-1 Suehiro, Kumagaya-shi, Saitama Stock company Riken Kumagaya Works
Claims (4)
する理論反応量より多い酸素とを含む燃焼排ガスから窒
素酸化物を除去する除去材において、多孔質の無機酸化
物に硫酸銀を銀元素に換算して0.2〜15重量%、又
は0.2〜15重量%の銀と銀のモル数の1/50〜2
倍の硫酸とを担持してなり、外部から前記排ガス中に添
加された炭化水素又は含酸素有機化合物を還元剤とし
て、200〜600℃で、前記排ガス中の窒素酸化物を
還元することを特徴とする窒素酸化物除去材。1. A removal material for removing nitrogen oxides from a combustion exhaust gas containing nitrogen oxides and oxygen in an amount larger than the theoretical reaction amount for coexisting unburned components, wherein silver sulfate is silver element as a porous inorganic oxide. 0.2 to 15% by weight or 0.2 to 15% by weight of silver and 1/50 to 2 of the number of moles of silver
It is characterized by supporting twice the amount of sulfuric acid and reducing the nitrogen oxides in the exhaust gas at 200 to 600 ° C. by using a hydrocarbon or an oxygen-containing organic compound externally added to the exhaust gas as a reducing agent. Nitrogen oxide removing material.
いて、前記多孔質の無機酸化物がアルミナ又はアルミナ
系複合酸化物であることを特徴とする窒素酸化物除去
材。2. The nitrogen oxide removing material according to claim 1, wherein the porous inorganic oxide is alumina or an alumina-based composite oxide.
材において、前記除去材はさらにセラミック製又は金属
製三次元構造体を含有し、前記多孔質無機酸化物が前記
三次元構造体にコートされていることを特徴とする窒素
酸化物除去材。3. The nitrogen oxide removing material according to claim 1 or 2, wherein the removing material further contains a ceramic or metal three-dimensional structure, and the porous inorganic oxide is the three-dimensional structure. Nitrogen oxide removing material characterized by being coated on.
する理論反応量より多い酸素とを含む燃焼排ガスから窒
素酸化物を除去する方法において、請求項1〜3のいず
れかに記載の窒素酸化物除去材を排ガス導管の途中に設
置し、前記除去材の上流側で前記排ガス中に炭化水素又
は含酸素有機化合物を添加し、200〜600℃で前記
排ガスを前記除去材に接触させ、前記炭化水素又は含酸
素有機化合物と前記窒素酸化物とを反応させて前記窒素
酸化物を除去することを特徴とする窒素酸化物除去方
法。4. A method for removing nitrogen oxides from a combustion exhaust gas containing nitrogen oxides and oxygen in a larger amount than the theoretical reaction amount for coexisting unburned components, the nitrogen oxidation according to claim 1. Substance removal material is installed in the middle of the exhaust gas conduit, hydrocarbons or oxygen-containing organic compounds are added to the exhaust gas on the upstream side of the removal material, and the exhaust gas is contacted with the removal material at 200 to 600 ° C., A method for removing nitrogen oxide, which comprises reacting a hydrocarbon or an oxygen-containing organic compound with the nitrogen oxide to remove the nitrogen oxide.
Priority Applications (7)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4360039A JPH06198131A (en) | 1992-12-28 | 1992-12-28 | Material for removing nitrogen oxide and method for removing nitrogen oxide |
EP19930310560 EP0605237B1 (en) | 1992-12-28 | 1993-12-24 | Exhaust gas cleaner |
DE1993609245 DE69309245T2 (en) | 1992-12-28 | 1993-12-24 | Exhaust gas cleaner |
US08/434,918 US5714432A (en) | 1992-12-28 | 1995-05-04 | Exhaust gas cleaner comprising supported silver or silver oxide particles |
US08/601,495 US5656249A (en) | 1992-12-28 | 1996-02-14 | Exhaust gas cleaner and method for removing nitrogen oxides |
US08/805,234 US5772973A (en) | 1992-12-28 | 1997-02-24 | Exhaust gas cleaner and method for removing nitrogen oxides |
US08/917,144 US5801117A (en) | 1992-12-28 | 1997-08-25 | Comprising supported silver sulfate or silver chloride or silver with sulfuric acid |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4360039A JPH06198131A (en) | 1992-12-28 | 1992-12-28 | Material for removing nitrogen oxide and method for removing nitrogen oxide |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH06198131A true JPH06198131A (en) | 1994-07-19 |
Family
ID=18467590
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP4360039A Pending JPH06198131A (en) | 1992-12-28 | 1992-12-28 | Material for removing nitrogen oxide and method for removing nitrogen oxide |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH06198131A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006007216A (en) * | 2004-06-24 | 2006-01-12 | Caterpillar Inc | Silver added catalyst for exhaust gas treatment |
WO2010013730A1 (en) * | 2008-07-29 | 2010-02-04 | バブコック日立株式会社 | Catalyst for cleaning up nitrogen oxides and a method for producing same |
JP2015196141A (en) * | 2014-04-02 | 2015-11-09 | 株式会社豊田中央研究所 | Exhaust gas purification catalyst, exhaust gas purification filter and exhaust gas purification method using the same |
WO2016190294A1 (en) * | 2015-05-25 | 2016-12-01 | トヨタ自動車株式会社 | Exhaust gas purifying catalyst, exhaust gas purifying filter using same and exhaust gas purification method |
-
1992
- 1992-12-28 JP JP4360039A patent/JPH06198131A/en active Pending
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006007216A (en) * | 2004-06-24 | 2006-01-12 | Caterpillar Inc | Silver added catalyst for exhaust gas treatment |
WO2010013730A1 (en) * | 2008-07-29 | 2010-02-04 | バブコック日立株式会社 | Catalyst for cleaning up nitrogen oxides and a method for producing same |
DE112009002108T5 (en) | 2008-07-29 | 2011-07-07 | Babcock-Hitachi K.K. | Catalyst for purifying nitrogen oxides and process for its preparation |
CN102123791A (en) * | 2008-07-29 | 2011-07-13 | 巴布考克日立株式会社 | Catalyst for cleaning up nitrogen oxides and a method for producing same |
US8664141B2 (en) | 2008-07-29 | 2014-03-04 | Babcock-Hitachi Kabushiki Kaisha | Catalyst for cleaning up nitrogen oxides and a method for producing same |
JP2015196141A (en) * | 2014-04-02 | 2015-11-09 | 株式会社豊田中央研究所 | Exhaust gas purification catalyst, exhaust gas purification filter and exhaust gas purification method using the same |
WO2016190294A1 (en) * | 2015-05-25 | 2016-12-01 | トヨタ自動車株式会社 | Exhaust gas purifying catalyst, exhaust gas purifying filter using same and exhaust gas purification method |
JP2016215160A (en) * | 2015-05-25 | 2016-12-22 | 株式会社豊田中央研究所 | Catalyst for exhaust gas purification, exhaust gas purification filter using the same, and exhaust gas purification method |
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