JPH1181988A - Exhaust emission control device for internal combustion engine - Google Patents
Exhaust emission control device for internal combustion engineInfo
- Publication number
- JPH1181988A JPH1181988A JP9239270A JP23927097A JPH1181988A JP H1181988 A JPH1181988 A JP H1181988A JP 9239270 A JP9239270 A JP 9239270A JP 23927097 A JP23927097 A JP 23927097A JP H1181988 A JPH1181988 A JP H1181988A
- Authority
- JP
- Japan
- Prior art keywords
- sox
- exhaust gas
- nox
- lean
- nox catalyst
- 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
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02T—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
- Y02T10/00—Road transport of goods or passengers
- Y02T10/10—Internal combustion engine [ICE] based vehicles
- Y02T10/12—Improving ICE efficiencies
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Exhaust Gas After Treatment (AREA)
- Treating Waste Gases (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は自動車等の内燃機関
から排出される排ガスを浄化する装置に係わり、特に希
薄空燃比燃焼(リーンバーン)可能な内燃機関から排出
される排ガスの浄化装置に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a device for purifying exhaust gas discharged from an internal combustion engine of an automobile or the like, and more particularly to a device for purifying exhaust gas discharged from an internal combustion engine capable of lean air-fuel ratio combustion (lean burn).
【0002】[0002]
【従来の技術】自動車等の内燃機関から排出される排ガ
スに含まれる、一酸化炭素(CO),炭化水素(HC:H
ydrocarbon),窒素酸化物(NOx)等は大気汚染物質
として人体に悪影響を及ぼす他、植物の生育を妨げる等
の問題を生起する。そこで、従来より、これらの排出量
低減には多大の努力が払われ、内燃機関の燃焼方法の改
善による発生量の低減に加え、排出された排ガスを触媒
等を利用して浄化する方法の開発が進められ、着実な成
果を挙げてきた。ガソリンエンジン車に関しては、三元
触媒なるPt,Rhを活性の主成分とし、HC及びCO
の酸化とNOxの還元を同時に行って無害化する触媒を
用いる方法が主流となっている。2. Description of the Related Art Carbon monoxide (CO) and hydrocarbons (HC: H) contained in exhaust gas discharged from an internal combustion engine of an automobile or the like are used.
Hydrocarbons, nitrogen oxides (NOx), and the like adversely affect the human body as air pollutants and cause problems such as hindering plant growth. So far, great efforts have been made to reduce these emissions, and in addition to reducing the amount generated by improving the combustion method of the internal combustion engine, a method of purifying the exhaust gas using a catalyst or the like has been developed. Has been promoted and has achieved steady results. For gasoline engine vehicles, Pt and Rh, which are three-way catalysts, are the main components of activity, and HC and CO
The mainstream is a method using a catalyst that renders harmless by simultaneously oxidizing NO and reducing NOx.
【0003】ところで、三元触媒はその特性から、ウィ
ンドウと称される理論空気燃料比近傍で燃焼させて生成
した排ガスにしか効果的に作用しない。そこで従来は、
空燃比は自動車の運転状況に応じて変動するものの変動
範囲は原則として理論空燃料(ガソリンの場合A(空気
の重量)/F(燃料の重量)=約14.7;以下本明細書
では理論空撚比をA/F=14.7 で代表させるが燃料
種によりこの数値は変る。)近傍に調節されてきた。し
かし、理論空燃比より希薄(リーン)な空燃比でエンジ
ンを運転できると燃費を向上させる事ができることか
ら、リーンバーン燃焼技術の開発が進められ、近年は理
論空燃比以上の空燃比で燃焼を行わせるリーンバーン車
や筒内噴射エンジン搭載車(Direct Injection車;以下
DI車)の開発が進み一部で実用化されている。しかし
前述の様に現用三元触媒でリーンバーン排ガス(以下リ
ーン排ガス)の浄化を行わせるとHC,COの酸化浄化
は行えるもののNOxを効果的に還元浄化することはで
きない。したがって、リーンバーン車およびDI車の本
格的普及のためにはリーンバーンで生成する排ガスの浄
化技術、すなわち酸素(O2 )が多量に含まれる排ガス
中のHC,NO,NOxを浄化する技術の開発、特にNO
xを浄化する技術の開発が不可欠となる。[0003] By the way, due to its characteristics, the three-way catalyst effectively acts only on exhaust gas generated by burning near the theoretical air-fuel ratio called a window. So conventionally,
Although the air-fuel ratio fluctuates according to the driving conditions of the vehicle, the fluctuation range is, in principle, the theoretical air fuel (A (weight of air) / F (weight of fuel) = about 14.7 in the case of gasoline; The air / twist ratio is represented by A / F = 14.7, but this value varies depending on the fuel type.) However, if the engine can be operated at an air-fuel ratio leaner than the stoichiometric air-fuel ratio, fuel efficiency can be improved, and lean burn combustion technology has been developed. In recent years, combustion at an air-fuel ratio higher than the stoichiometric air-fuel ratio has been promoted. The development of lean burn vehicles and vehicles equipped with in-cylinder injection engines (Direct Injection vehicles; hereinafter referred to as DI vehicles) have been advanced and some of them have been put to practical use. However, as described above, when lean burn exhaust gas (hereinafter referred to as "lean exhaust gas") is purified by a current three-way catalyst, HC and CO can be oxidized and purified, but NOx cannot be effectively reduced and purified. Therefore, for full-fledged use of lean burn vehicles and DI vehicles, a technology for purifying exhaust gas generated by lean burn, that is, a technology for purifying HC, NO, and NOx in exhaust gas containing a large amount of oxygen (O 2 ). Development, especially NO
It is essential to develop a technology for purifying x.
【0004】本課題を解決すべく、新規な触媒および触
媒システムの開発が進められ、その一つにリーン排ガス
中のNOxを吸着,吸収あるいは吸蔵等の方法で一旦捕
捉し、還元雰囲気中で該捕捉NOxを還元し浄化する方
法がある。この方法は例えば、特開昭62−97630 号,特
開昭62−106826号,特開昭62−117620号および日本国特
許第2600492 号に提示されている。In order to solve this problem, the development of a new catalyst and a catalyst system has been promoted. One of them is to once capture NOx in lean exhaust gas by a method such as adsorption, absorption or occlusion, and to obtain the NOx in a reducing atmosphere. There is a method of reducing and purifying trapped NOx. This method is disclosed, for example, in JP-A-62-97630, JP-A-62-106826, JP-A-62-117620 and Japanese Patent No. 2600492.
【0005】この方法の実用上の課題の一つに硫黄化合
物による被毒がある。[0005] One of the practical problems of this method is poisoning by sulfur compounds.
【0006】ガソリン等の化石燃料中には硫黄(S)が
含まれ、燃焼排ガス中では硫黄は主としてSOxとして
存在する。SOxは二酸化硫黄(SO2)と三酸化硫黄(S
O3)からなるが通常前者が大部分である。SOxは前記
NOx捕捉材と結合し易く、しかも通常NOxより結合
力が強い。従って、SOxがNOx捕捉材に捕捉されN
Ox捕捉サイトを占めるとNOx捕捉能力が大幅に低下
しついには捕捉能力を示さなくなる、いわゆるSOx被
毒現象が生じる。[0006] Sulfur (S) is contained in fossil fuels such as gasoline, and sulfur is mainly present as SOx in combustion exhaust gas. SOx is composed of sulfur dioxide (SO 2 ) and sulfur trioxide (S
O 3 ), but the former is usually the majority. SOx is easily bonded to the NOx trapping material, and has a stronger binding force than NOx. Therefore, SOx is trapped by the NOx trapping material and N
When occupying the Ox trapping site, the so-called SOx poisoning phenomenon occurs, in which the NOx trapping ability is greatly reduced and eventually no longer shows the trapping ability.
【0007】そこで本課題を解決するため、例えば、特
開平8−281116 号にリン酸ジルコニウムを担体とするN
Ox捕捉材が、特開平9−926号にTiとZrとAlの複
合酸化物を担体とするNOx捕捉材が、特開平6−66129
号,特開平9−32619号、にSOx被毒したNOx捕捉材
の再生装置等が提案されている。しかし、これらは、S
Ox被毒問題の軽減に有効であるものの、効果が限定さ
れている他、装置が複雑になる等の問題もあり、さらに
実用性の高い方法を求めて検討が続けられているのが実
状である。In order to solve this problem, for example, Japanese Patent Application Laid-Open No. 8-281116 discloses an N-type carrier containing zirconium phosphate as a carrier.
An Ox trapping material is disclosed in JP-A-9-926, and a NOx trapping material using a composite oxide of Ti, Zr and Al as a carrier is disclosed in JP-A-6-66129.
JP-A-9-32619 proposes an apparatus for regenerating a SOx-poisoned NOx trapping material. However, these are
Although effective in reducing the problem of Ox poisoning, in addition to the limited effects, there are also problems such as the complexity of the device. In fact, studies have been continued in search of more practical methods. is there.
【0008】[0008]
【発明が解決しようとする課題】本発明は、上記従来技
術の問題点に鑑み、SOx被毒を効果的に防止できかつ
実用性に優れた、内燃機関のリーンバーン排ガスからN
Ox等の有害成分を除去、無害化できる装置を提供する
ことにある。SUMMARY OF THE INVENTION In view of the above-mentioned problems of the prior art, an object of the present invention is to reduce SOx poisoning and effectively reduce the amount of N2 from lean burn exhaust gas of an internal combustion engine.
It is an object of the present invention to provide an apparatus capable of removing and detoxifying harmful components such as Ox.
【0009】[0009]
【課題を解決するための手段】上記課題の解決方法とし
て、内燃機関の排ガス流路にSOx捕捉材を設けその後
流にリーンNOx触媒を設ける方法が考えられる。この
方法は、SOx捕捉材のSOx捕捉能力が高いことが先
ず必要となる。またこの方法ではSOxが捕捉材に蓄積
し、やがてSOx捕捉能力を失うことから捕捉材の再生
が不可欠となる。そこで捕捉材の再生が容易に行えるこ
とが必須となる。また、後述するように、再生操作で排
出された硫黄化合物が後流に位置するリーンNOx触媒
の被毒を生じないことあるいは被毒が少なく容易に再生
できることが必要となる。As a solution to the above-mentioned problem, a method is conceivable in which an SOx trapping material is provided in an exhaust gas passage of an internal combustion engine and a lean NOx catalyst is provided downstream of the SOx trapping material. This method first requires that the SOx trapping material has a high SOx trapping ability. Further, in this method, SOx accumulates in the trapping material and eventually loses the SOx trapping ability, so that regeneration of the trapping material is indispensable. Therefore, it is essential that the trapping material can be easily regenerated. Further, as described later, it is necessary that the sulfur compound discharged in the regeneration operation does not cause poisoning of the lean NOx catalyst located downstream, or that the NOx catalyst can be easily regenerated with little poisoning.
【0010】本発明者は上記の各課題を解決して本発明
に至った。The present inventor has solved the above-mentioned problems and has accomplished the present invention.
【0011】本発明では上記各課題を以下の各方法によ
り解決する。In the present invention, the above objects are solved by the following methods.
【0012】本発明の最大の特徴は、内燃機関排ガス流
路に、排ガス中のSOxを吸着,吸収等の方法により捕
捉し、捕捉した温度より高い温度でかつ排ガスに含まれ
る酸化剤と還元剤の酸化還元化学量論関係において酸化
剤に対し還元剤が同量以上(以下還元雰囲気)の場合に
捕捉したSOxを脱着あるいは放出するSOx捕捉材を
設け、その後流に、排ガスに含まれる酸化剤と還元剤の
酸化還元化学量論関係において還元剤に対して酸化剤が
多い(以下酸化雰囲気)場合に排ガス中の炭化水素(H
C)と一酸化炭素(CO)を酸化浄化すると同時にNO
xを吸着,吸収等の方法で捕捉し、還元雰囲気において
捕捉したNOxを接触還元してNOx捕捉能を回復する
と同時に排ガス中のNOxの還元浄化とHC(炭化水
素),CO(一酸化炭素)の酸化浄化を行うリーンNOx
触媒を設け、還元雰囲気下でSOx捕捉材を昇温してS
Ox捕捉能を回復させることを特徴とする排ガス浄化装
置にある。The most significant feature of the present invention is that SOx in exhaust gas is trapped in an exhaust gas passage of an internal combustion engine by a method such as adsorption or absorption, and an oxidizing agent and a reducing agent at a temperature higher than the trapped temperature and contained in the exhaust gas. In the redox stoichiometry, an SOx trapping material for desorbing or releasing trapped SOx when the amount of the reducing agent is equal to or more than that of the oxidizing agent (hereinafter referred to as a reducing atmosphere) is provided. When there is a large amount of oxidizing agent relative to the reducing agent (hereinafter referred to as oxidizing atmosphere) in the redox stoichiometric relationship between
C) and at the same time oxidize and purify carbon monoxide (CO)
x is trapped by a method such as adsorption or absorption, and the NOx trapped in a reducing atmosphere is contact-reduced to restore the NOx trapping ability, while at the same time reducing and purifying NOx in the exhaust gas and HC (hydrocarbon), CO (carbon monoxide). NOx that purifies oxidized water
A catalyst is provided, and the SOx trapping material is heated in a reducing atmosphere to increase S
An exhaust gas purification apparatus characterized by restoring Ox trapping ability.
【0013】ここで、酸化剤はO2 、一酸化窒素(N
O),二酸化窒素(NO2 )等で主としてO2 である。
還元剤は、内燃機関に供されたHC、燃焼過程で生成す
るその派生物としてのHC(含む含酸素炭化水素),C
O,水素(H2 )等、さらには、後述の還元成分として
排ガス中に添加されるHC等の還元性物質である。Here, the oxidizing agent is O 2 , nitric oxide (N
O), nitrogen dioxide (NO 2 ), etc., which are mainly O 2 .
The reducing agent is HC supplied to the internal combustion engine, HC (including oxygen-containing hydrocarbon) as a derivative thereof generated in the combustion process, C
O, hydrogen (H 2 ), and other reducing substances such as HC added to exhaust gas as a reducing component described later.
【0014】排ガス中のSOxは一般に大部のSO2 と
一部のSO3 から成る。したがって、これらを亜硫酸塩
および/または硫酸塩とすることにより効果的に捕捉す
ることができる。[0014] SOx in the exhaust gas is generally composed of SO 2 and part of SO 3 voluminous. Therefore, these can be effectively trapped by converting them into sulfites and / or sulfates.
【0015】本目的を達するSOx捕捉材には、リチウ
ム(Li),カリウム(K),ナトリウム(Na)等の
アルカリ金属、及びマグネシウム(Mg),カルシウム
(Ca),ストロンチウム(Sr),バリウム(Ba)等
のアルカリ土類金属、及びアルミニウム(Al)、及び
チタン(Ti)、及びバナジウム(V),クロム(C
r),マンガン(Mn),鉄(Fe),コバルト(C
o),ニッケル(Ni),銅(Cu),亜鉛(Zn)等
の第一遷移元素、及びランタン(La),セリウム(C
e)等の希土類金属、から選ばれる少なくとも一種の元
素、を含む金属および金属酸化物(もしくは複合酸化
物)からなる組成物、該組成物を多孔質耐熱性金属酸化
物に担持してなる組成物が適用できる。The SOx trapping material that achieves this object includes alkali metals such as lithium (Li), potassium (K) and sodium (Na), and magnesium (Mg) and calcium.
(Ca), strontium (Sr), alkaline earth metals such as barium (Ba), aluminum (Al), titanium (Ti), vanadium (V), chromium (C
r), manganese (Mn), iron (Fe), cobalt (C
o), first transition elements such as nickel (Ni), copper (Cu), zinc (Zn), lanthanum (La), cerium (C
e) a composition comprising a metal containing at least one element selected from rare earth metals such as e) and a metal oxide (or composite oxide), and a composition comprising the composition supported on a porous heat-resistant metal oxide Things can be applied.
【0016】以上のSOx捕捉材において、排ガス中の
SO2 は亜硫酸塩となり、SO3 は硫酸塩となる。亜硫
酸塩は排ガスに含まれるO2 により酸化されて一部が硫
酸塩に変化する。当然であるが、排ガスがリーンバーン
排ガスで酸化雰囲気の場合、亜硫酸塩の酸化は進み易
い。SO3 は前述のように硫酸塩として捕捉される。な
お、SO3 の一部は排ガス中の水蒸気と結合して硫酸と
なりSOx捕捉材に付着するかもしくは硫酸ミストとし
て飛散するものがある。何れにせよ、SOx捕捉剤に捕
捉されたSOxは主として亜硫酸塩と硫酸塩として存在
する。In the above SOx trapping material, SO 2 in the exhaust gas becomes a sulfite and SO 3 becomes a sulfate. The sulfite is oxidized by O 2 contained in the exhaust gas and partly changes to sulfate. As a matter of course, when the exhaust gas is a lean burn exhaust gas in an oxidizing atmosphere, the oxidation of the sulfite easily proceeds. SO 3 is captured as a sulfate as described above. Some of the SO 3 is combined with the water vapor in the exhaust gas to form sulfuric acid, which is attached to the SOx trapping material or scattered as a sulfuric acid mist. In any case, SOx trapped by the SOx trapping agent exists mainly as sulfite and sulfate.
【0017】また、本発明におけるSOx捕捉材には、
リチウム(Li),カリウム(K),ナトリウム(N
a)等のアルカリ金属、及びマグネシウム(Mg),カ
ルシウム(Ca),ストロンチウム(Sr),バリウム
(Ba)等のアルカリ土類金属、及びチタン(Ti)、
及びアルミニウム(Al)、及びバナジウム(V),ク
ロム(Cr),マンガン(Mn),鉄(Fe),コバル
ト(Co),ニッケル(Ni),銅(Cu),亜鉛(Z
n)等の第一遷移元素、及びランタン(La),セリウ
ム(Ce)等の希土類金属、から選ばれる少なくとも一
種の元素と、白金(Pt),ロジウム(Rh),パラヂ
ウム(Pd)等の貴金属から選ばれる少なくとも一種の
元素、を含む金属および金属酸化物(もしくは複合酸化
物)からなる組成物、該組成物を多孔質耐熱性金属酸化
物に担持してなる組成物、が適用できる。Further, the SOx trapping material of the present invention includes:
Lithium (Li), potassium (K), sodium (N
a) and alkaline earth metals such as magnesium (Mg), calcium (Ca), strontium (Sr) and barium (Ba), and titanium (Ti);
And aluminum (Al), and vanadium (V), chromium (Cr), manganese (Mn), iron (Fe), cobalt (Co), nickel (Ni), copper (Cu), zinc (Z
n) and at least one element selected from rare earth metals such as lanthanum (La) and cerium (Ce), and noble metals such as platinum (Pt), rhodium (Rh) and palladium (Pd). A composition comprising a metal containing at least one element selected from the group consisting of a metal and a metal oxide (or a composite oxide), and a composition comprising the composition supported on a porous heat-resistant metal oxide can be used.
【0018】本組成物は前記組成物に白金(Pt),ロ
ジウム(Rh),パラヂウム(Pd)等の貴金属を添加し
たことに特徴がある。本SOx捕捉材においては、SO
xの捕捉にあたり、特に酸化雰囲気の場合、SO2 をS
O3 として捕捉する機能が強化される。その結果SOx
捕捉能が強化される。The present composition is characterized in that a precious metal such as platinum (Pt), rhodium (Rh), palladium (Pd) or the like is added to the above composition. In the present SOx trapping material, SO
When capturing x, SO 2 is converted to S
The ability to capture as O 3 is enhanced. As a result, SOx
Capture ability is enhanced.
【0019】さらに、本発明におけるSOx捕捉材とし
て、アルミニウム(Al)、及びバナジウム(V),ク
ロム(Cr),マンガン(Mn),鉄(Fe),コバル
ト(Co),ニッケル(Ni),銅(Cu),亜鉛(Z
n)等の第一遷移元素、及びランタン(La),セリウ
ム(Ce)等の希土類金属、から選ばれる少なくとも一
種の元素と、白金(Pt),ロジウム(Rh),パラヂ
ウム(Pd)等の貴金属から選ばれる少なくとも1種の
元素、を含む金属および金属酸化物(もしくは複合酸化
物)からなる組成物、該組成物を多孔質耐熱性金属酸化
物に担持してなる組成物が適用できる。Further, as the SOx trapping material in the present invention, aluminum (Al), vanadium (V), chromium (Cr), manganese (Mn), iron (Fe), cobalt (Co), nickel (Ni), copper (Cu), zinc (Z
n) and at least one element selected from rare earth metals such as lanthanum (La) and cerium (Ce), and noble metals such as platinum (Pt), rhodium (Rh) and palladium (Pd). A composition comprising a metal containing at least one element selected from the group consisting of a metal and a metal oxide (or a composite oxide), and a composition comprising the composition supported on a porous heat-resistant metal oxide can be used.
【0020】本SOx捕捉材においてSOxは貴金属の
触媒作用でSO3 となり遷移金属硫酸塩として捕捉され
る。例えば、第一遷移元素であるAlの安定な酸化物A
l2O3は硫酸アルミニウム(Al2(SO4)3)となっ
てSOxを捕捉する。また、希土類金属であるCeの安
定な酸化物CeO2 はCe(SO4)2となってSOxを捕
捉する。これらの硫酸塩はアルカリ金属及びアルカリ土
類金属の硫酸塩より還元雰囲気において再生され易い。In the present SOx trapping material, SOx is converted into SO 3 by the catalytic action of the noble metal and trapped as a transition metal sulfate. For example, a stable oxide A of the first transition element Al
l 2 O 3 becomes aluminum sulfate (Al 2 (SO 4 ) 3 ) to capture SOx. In addition, CeO 2, a stable oxide of Ce, which is a rare earth metal, becomes Ce (SO 4 ) 2 and captures SOx. These sulfates are more easily regenerated in reducing atmospheres than alkali metal and alkaline earth metal sulfates.
【0021】従って、再生にあたって行う昇温の程度が
小さくなるという特徴がある。Therefore, there is a feature that the degree of temperature increase performed in the regeneration is reduced.
【0022】以上のSOx捕捉材において、SOxを捕
捉して減退したSOx捕捉能は、SOx捕捉時より高い
温度でかつ還元雰囲気下に置くことにより回復する。本
発明の方法においては、SOx捕捉材をNOx捕捉材よ
り上流に置くことによりこの温度条件の達成を容易とす
る。In the above-mentioned SOx trapping material, the SOx trapping ability reduced by trapping SOx is restored by placing the SOx trapping material at a higher temperature than in the SOx trapping and in a reducing atmosphere. In the method of the present invention, placing the SOx trapping material upstream of the NOx trapping material facilitates achieving this temperature condition.
【0023】SOx捕捉能の回復はSO2 を放出して以
下のように進む。尚、以下では、SOx捕捉成分をアル
カリ金属Mで、還元剤を炭化水素(HC)で代表させ
た。 [硫酸塩の亜硫酸塩化]Recovery of the SOx trapping ability releases SO 2 and proceeds as follows. In the following, the SOx trapping component is represented by alkali metal M, and the reducing agent is represented by hydrocarbon (HC). [Sulfite sulfation]
【0024】[0024]
【化1】M2SO4+HC→M2SO3+CO2 M:SOx捕捉金属成分 HC:還元剤成分 [亜硫酸塩のSOx捕捉能回復]## STR1 ## M 2 SO 4 + HC → M 2 SO 3 + CO 2 M: SOx trapping metal component HC: Reducing agent component [Recovery of SOx trapping ability of sulfite]
【0025】[0025]
【化2】M2SO3+HC→M2O+SO2 ## STR2 ## M 2 SO 3 + HC → M 2 O + SO 2
【0026】[0026]
【化3】 M2O+CO2→M2CO3(SOx捕捉成分) 放出されたSO2 は還元雰囲気のガス中に含まれ後流に
位置するリーンNOx触媒に達する。本発明ではこの放
出SO2 によるリーンNOx触媒のSOx被毒を以下の
材料及び方法で防止する。Embedded image M 2 O + CO 2 → M 2 CO 3 (SOx trapping component) The released SO 2 is contained in the gas of the reducing atmosphere and reaches the lean NOx catalyst located downstream. The present invention prevents the SOx poisoning of the lean NOx catalyst according to the release SO 2 in the following materials and methods.
【0027】本目的を達するリーンNOx触媒は、リチ
ウム(Li),ナトリウム(Na),カリウム(K),
マグネシウム(Mg),ストロンチウム(Sr),バリ
ウム(Ba)及びカルシウム(Ca)から選ばれる少なく
とも一種と、セリウム(Ce)等からなる希土類から選ば
れる少なくとも一種と、白金(Pt),ロジウム(Rh),
パラヂウム(Pd)等の貴金属から選ばれる少なくとも
一種の元素を含み、必要に応じてシリカ(Si),チタ
ン(Ti),ジルコニウム(Zr)から選ばれる少なく
とも一種の元素を含む、金属および金属酸化物(もしく
は複合酸化物)からなる組成物、該組成物を多孔質耐熱
性金属酸化物に担持してなる組成物である。The lean NOx catalyst which achieves the object is composed of lithium (Li), sodium (Na), potassium (K),
At least one selected from magnesium (Mg), strontium (Sr), barium (Ba) and calcium (Ca), at least one selected from rare earths such as cerium (Ce), platinum (Pt), rhodium (Rh) ,
Metals and metal oxides containing at least one element selected from noble metals such as palladium (Pd) and, if necessary, at least one element selected from silica (Si), titanium (Ti) and zirconium (Zr) (Or a composite oxide) and a composition obtained by supporting the composition on a porous heat-resistant metal oxide.
【0028】再生により生じたSO2 を含む排ガスは上
記リーンNOx触媒と接触するが以下の理由でSO2 捕
捉量は少ない。すなわちSOx被毒はあまり受けない。Exhaust gas containing SO 2 generated by regeneration comes into contact with the lean NOx catalyst, but the amount of SO 2 captured is small for the following reasons. That is, SOx poisoning is not much received.
【0029】先ず、SO2 の結合力はSO3 に比べて弱
い。また、SO2 は還元雰囲気中にありSO3 に転化し
て捕捉されることがない。さらに、SO2 の接触時間と
濃度は、排ガスが直接通過する場合に比べて、短時間か
つ高濃度である。さらに、SOx捕捉材の再生にあたり
SOx捕捉材が昇温されており、SO2 を含む排ガス温
度は高まっている。First, the bonding force of SO 2 is weaker than that of SO 3 . Also, SO 2 is in a reducing atmosphere and is not converted to SO 3 and captured. Furthermore, the contact time and concentration of SO 2 are shorter and higher concentration than when exhaust gas passes directly. Further, SOx trapping agent Upon regeneration of the SOx trapping agent are heated, the temperature of the exhaust gas containing SO 2 is increasing.
【0030】さらに、必要に応じてSOx捕捉材を昇温
することによりSO2 被毒を完全に防止することができ
る。この場合、昇温は必要であるが、SO2 はSO2 の
まま吸着あるいは亜硫酸塩として捕捉されているため、
SOx捕捉材の再生に要する温度より低い温度で十分で
ある。Further, SO 2 poisoning can be completely prevented by raising the temperature of the SOx trapping material as required. In this case, it is necessary to raise the temperature, but since SO 2 is adsorbed as SO 2 or trapped as sulfite,
A temperature lower than the temperature required for regeneration of the SOx trapping material is sufficient.
【0031】本発明の方法における、燃焼排ガス中で酸
化剤に対して還元剤が同量かもしくは多い状態(酸化雰
囲気)は、以下の方法でつくる事ができる。In the method of the present invention, the state in which the amount of the reducing agent is equal to or larger than the amount of the oxidizing agent in the combustion exhaust gas (oxidizing atmosphere) can be prepared by the following method.
【0032】内燃機関における燃焼条件を理論空燃比も
しくは燃料過剰(リッチ)とする。また、希薄燃焼で生
じたリーンバーン排ガスに還元剤を添加することによっ
ても可能である。The combustion conditions in the internal combustion engine are set to the stoichiometric air-fuel ratio or excess fuel (rich). It is also possible to add a reducing agent to lean burn exhaust gas generated by lean combustion.
【0033】前者は以下の方法で達成することができ
る。The former can be achieved by the following method.
【0034】排気ダクトに設けられた酸素濃度センサー
の出力及び吸気流量センサーの出力等に応じて燃料噴射
量を制御する方法。本法では、複数の気筒の一部を燃料
過剰とし残部を燃料不足とし、全気筒からの混合排ガス
中の成分が酸化還元化学量論関係において酸化剤に対し
て還元剤が同量かもしくは多い状態をつくる方法をも含
む。A method of controlling the fuel injection amount according to the output of an oxygen concentration sensor provided in an exhaust duct, the output of an intake air flow sensor, and the like. In this method, a part of the plurality of cylinders is made excessive and the remaining fuel is made insufficient, and the components in the mixed exhaust gas from all the cylinders have the same amount or larger amount of the reducing agent than the oxidizing agent in the oxidation-reduction stoichiometry relationship. Includes methods for creating states.
【0035】後者は以下の各方法で達成することができ
る。The latter can be achieved by the following methods.
【0036】排ガス流のSOx捕捉剤の上流に還元剤を
投入する方法。還元剤には内燃機関の燃料としてのガソ
リン,軽油,灯油,天然ガス、これらの改質物,水素,
アルコール類,アンモニア等が適用できる。ブローバイ
ガス及びキャニスターパージガスをSOx捕捉材上流に
導き、これらに含まれる炭化水素等の還元剤を投入する
ことも有効である。燃料直噴式内燃機関においては、排
気行程で燃料を噴射し還元剤としての燃料を投入するこ
とが有効である。A method of introducing a reducing agent upstream of the SOx trapping agent in the exhaust gas stream. Gasoline, light oil, kerosene, natural gas, their reformed products, hydrogen,
Alcohols, ammonia, etc. can be applied. It is also effective to guide the blow-by gas and the canister purge gas upstream of the SOx trapping material, and to introduce a reducing agent such as a hydrocarbon contained therein. In a fuel direct injection type internal combustion engine, it is effective to inject fuel during an exhaust stroke and to input fuel as a reducing agent.
【0037】本発明における、SOx捕捉材及びリーン
NOx触媒の多孔質耐熱性金属酸化物には、アルミナ
(Al2O3),チタニア(TiO2),ジルコニア(Z
rO2)等の金属酸化物、これら相互の複合金属酸化
物、を始めとする各種の金属酸化物及び複合金属酸化物
が適用できる。In the present invention, alumina (Al 2 O 3 ), titania (TiO 2 ) and zirconia (Z) are used as the porous heat-resistant metal oxide of the SOx trapping material and the lean NOx catalyst.
Various metal oxides and composite metal oxides including metal oxides such as rO 2 ), mutual metal oxides thereof, and the like can be applied.
【0038】本発明における、SOx捕捉材及びリーン
NOx触媒は、各種の形状で適用することができる。コ
ージェライト,ステンレス等の金属材料からなるハニカ
ム状構造体に吸着触媒成分をコーティングして得られる
ハニカム形状を始めとし、ペレット状,板状,粒状,粉
末として適用できる。In the present invention, the SOx trapping material and the lean NOx catalyst can be applied in various shapes. The present invention can be applied as a pellet, plate, granule, or powder, including a honeycomb shape obtained by coating a honeycomb-like structure made of a metal material such as cordierite or stainless steel with an adsorption catalyst component.
【0039】[0039]
【発明の実施の形態】本発明の具体的実施態様を挙げて
本発明を詳細に説明する。なお、本発明は以下の実施態
様及び実施例に限定されるものでなく、その思想範囲内
において各種の実施態様があることは言うまでもない。DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described in detail with reference to specific embodiments of the present invention. The present invention is not limited to the following embodiments and examples, and it goes without saying that there are various embodiments within the scope of the idea.
【0040】[排ガス浄化装置]図1は本発明の排ガス
浄化装置の一実施態様を示す装置の全体構成図である。
本発明の装置は、リーンバーン可能なエンジン99,エ
アフローセンサー2,スロットルバルブ3等を擁する吸
気系、酸素濃度センサー(or A/Fセンサー)19,排
ガス流路に設けられたSOx捕捉材17,リーンNOx
触媒18等を擁する排気系及び制御ユニット(ECU)
等から構成される。[Exhaust Gas Purification Apparatus] FIG. 1 is an overall configuration diagram of an apparatus showing one embodiment of an exhaust gas purification apparatus of the present invention.
The apparatus of the present invention includes an engine 99 capable of lean burn, an intake system having an air flow sensor 2, a throttle valve 3, etc., an oxygen concentration sensor (or A / F sensor) 19, an SOx trapping material 17 provided in an exhaust gas flow path, Lean NOx
Exhaust system and control unit (ECU) having catalyst 18 etc.
And so on.
【0041】以上の排気浄化装置は、以下のように機能
する。エンジンへの吸入空気はエアクリーナ1により濾
過された後エアフローセンサー2により計量され、スロ
ットルバルブ3を経て、さらにインジェクタ5から燃料
噴射を受け、混合気としてエンジン99に供給される。
エアフローセンサー信号その他のセンサー信号はECU(E
ngine Control Unit)へ入力される。The above exhaust gas purifying device functions as follows. The intake air to the engine is filtered by an air cleaner 1 and then measured by an air flow sensor 2, passes through a throttle valve 3, receives a fuel injection from an injector 5, and is supplied to the engine 99 as a mixture.
The airflow sensor signal and other sensor signals are
ngine Control Unit).
【0042】ECUでは各種の内燃機関の運転状態及び
リーンNOx触媒の状態を評価して運転空燃比を決定
し、インジェクタ5の噴射時間等を制御して混合気の燃
料濃度を所定値に設定する。シリンダーに吸入された混
合気はECU25からの信号で制御される点火プラグ1
0により着火され燃焼する。燃焼排ガスは排気系に導か
れる。排気系には先ずSOx捕捉材17が設けられその
後流にリーンNOx触媒18が設けてある。排ガスはS
Ox捕捉材でSOxを除去された後リーンNOx触媒に
達し、理論空燃比(ストイキ)運転時にはその三元触媒
機能により排ガス中のNOx,HC,COを浄化し、ま
た、リーンバーン運転時(酸化雰囲気排ガスを生成す
る)にはNOx捕捉能によりNOxを浄化すると同時に
併せ持つ触媒機能により、HCとCOを酸化浄化すると
同時に、NOxの一部を還元浄化する。さらに、各種の
センサー信号及びそれに基づくECUの判定により、リ
ーンバーン運転時にはリーンNOx触媒のNOx浄化能
力を常時評価して、NOx浄化能力が低下した場合、燃
焼の空燃比等をリッチ側にシフト(還元雰囲気排ガスを
生成)して、リーンNOx触媒のNOx吸着能を回復さ
せる。以上の操作により、本装置では、リーン運転,ス
トイキ(含むリッチ)運転の全てのエンジン燃焼条件下
における排ガスを効果的に浄化する。さらに、各種のセ
ンサー信号及びそれに基づくECUの判定により、リッ
チ運転後もNOx浄化能が十分に回復しないと評価され
た場合、あるいは燃料消費量等を勘案して決定される所
定のタイミングにより、SOx捕捉材の再生を行う。再
生は空燃比等をリッチ側にシフトして排ガスを還元雰囲
気とし、同時にSOx捕捉材を昇温することで行う。S
Ox捕捉材の昇温はエンジン回転数を上昇させることで
達成できる。さらに、SOx捕捉材の再生操作後もNO
x浄化能が十分に回復しない場合、リーンNOx触媒の
再生を行う。再生は空燃比等をリッチ側にシフトして還
元雰囲気排ガスをつくり、同時にSOx捕捉材を昇温す
ることで行う。リーンNOx触媒の昇温はエンジン回転
数を上昇させることで達成できる。The ECU evaluates the operating state of various internal combustion engines and the state of the lean NOx catalyst to determine the operating air-fuel ratio, and controls the injection time of the injector 5 to set the fuel concentration of the mixture to a predetermined value. . The air-fuel mixture sucked into the cylinder is a spark plug 1 controlled by a signal from the ECU 25.
It is ignited by 0 and burns. The combustion exhaust gas is led to an exhaust system. The exhaust system is provided with a SOx trapping material 17 first, and a lean NOx catalyst 18 provided downstream thereof. Exhaust gas is S
After the SOx is removed by the Ox trapping material, the catalyst reaches the lean NOx catalyst, and purifies NOx, HC, and CO in the exhaust gas by the three-way catalytic function during the stoichiometric air-fuel ratio (stoichiometric) operation. Atmospheric exhaust gas is generated) by purifying NOx with NOx trapping ability and simultaneously oxidizing and purifying HC and CO by a catalytic function which is combined with NOx, and at the same time, reducing and purifying a part of NOx. Further, the NOx purification performance of the lean NOx catalyst is constantly evaluated during the lean burn operation based on the various sensor signals and the determination by the ECU based on the various sensor signals. If the NOx purification performance decreases, the air-fuel ratio of the combustion is shifted to the rich side ( (Reducing atmosphere exhaust gas) to recover the NOx adsorption capacity of the lean NOx catalyst. Through the above operation, the present apparatus effectively purifies exhaust gas under all engine combustion conditions of lean operation and stoichiometric (including rich) operation. Further, when it is evaluated that the NOx purification performance does not sufficiently recover even after the rich operation based on various sensor signals and the determination of the ECU based on the various sensor signals, or at a predetermined timing determined in consideration of fuel consumption and the like, the SOx Regenerate the trapping material. The regeneration is performed by shifting the air-fuel ratio or the like to the rich side to make the exhaust gas a reducing atmosphere, and simultaneously raising the temperature of the SOx trapping material. S
The temperature rise of the Ox trapping material can be achieved by increasing the engine speed. Further, NO is maintained even after the SOx trapping material is regenerated.
If the x purification ability does not sufficiently recover, the lean NOx catalyst is regenerated. The regeneration is performed by shifting the air-fuel ratio and the like to the rich side to produce a reducing atmosphere exhaust gas, and simultaneously raising the temperature of the SOx trapping material. The temperature rise of the lean NOx catalyst can be achieved by increasing the engine speed.
【0043】[SOx捕捉材]本発明の方法によるSO
x捕捉材の調製例を示す。[SOx trapping material]
An example of preparing an x-capture material will be described.
【0044】《SOx捕捉材例1》SOx捕捉材T−1
を以下の方法で得た。<< SOx Capture Material Example 1 >> SOx Capture Material T-1
Was obtained in the following manner.
【0045】アルミナ粉末とベーマイトを硝酸邂逅して
得たバインダーとしてのアルミナゾルを混合し硝酸酸性
アルミナスラリーを得た。該コーティング液にセル数4
00cell/in2 のコーディエライト製ハニカムを浸漬し
た後速やかに引き上げ、セル内に閉塞した液をエアーブ
ローして除去した後、乾燥、続いて450℃で焼成し
た。この操作を繰返しハニカムの見掛け容積1Lあたり
150gのアルミナをコーティングした。該アルミナコ
ートハニカムに硝酸セリウム(硝酸Ce)溶液を含浸し
乾燥後600℃で1時間焼成した。続いて硝酸ナトリウ
ム(硝酸Na)溶液とチタニアゾル溶液と硝酸マグネシウ
ム(硝酸Mg)溶液の混合溶液を含浸し、同様に乾燥,焼
成した。以上によりアルミナ(Al2O3)にCe,Mg,
Na,Tiを担持したハニカム状SOx捕捉材、(18
Na,4Ti,2Mg)−27Ce/Al2O3を得た。
ここで、/Al2O3は各成分がAl2O3上に担持された
ことを示し、元素記号前の数値はハニカム見掛け容積1
L当たりに担持した表示金属成分の重量(g)である。
表記順序は担持順序を示しており、Al2O3に近く表記
される成分から離れる成分の順で担持し、( )で括ら
れた成分は同時に担持した。以下、SOx捕捉材とリー
ンNOx触媒の組成及び構成はこの表記法に従った。An alumina sol as a binder obtained by mixing alumina powder and boehmite in nitric acid was mixed to obtain a nitric acid acidic alumina slurry. 4 cells in the coating liquid
A 00 cell / in 2 honeycomb made of cordierite was immersed and then immediately pulled up, and the liquid clogged in the cells was removed by air blowing, dried, and subsequently fired at 450 ° C. This operation was repeated to coat 150 g of alumina per 1 L of apparent volume of the honeycomb. The alumina-coated honeycomb was impregnated with a cerium nitrate (Ce nitrate) solution, dried, and fired at 600 ° C. for 1 hour. Subsequently, a mixed solution of a sodium nitrate (Na nitrate) solution, a titania sol solution, and a magnesium nitrate (Mg nitrate) solution was impregnated, and dried and fired similarly. As described above, Ce, Mg, and alumina are added to alumina (Al 2 O 3 ).
Honeycomb SOx trapping material supporting Na and Ti, (18
To give Na, 4Ti, the 2Mg) -27Ce / Al 2 O 3 .
Here, / Al 2 O 3 indicates that each component was supported on Al 2 O 3 , and the numerical value before the element symbol indicates the honeycomb apparent volume 1
It is the weight (g) of the indicated metal component carried per L.
The notation order indicates the order in which the components are carried, and the components separated from the components near Al 2 O 3 are carried in order, and the components enclosed in parentheses are carried simultaneously. Hereinafter, the composition and configuration of the SOx trapping material and the lean NOx catalyst followed this notation.
【0046】《SOx捕捉材例2》SOx捕捉材T−2
を以下の方法で得た。<< SOx Capture Material Example 2 >> SOx Capture Material T-2
Was obtained in the following manner.
【0047】T−1と同じ方法で(18Na,4Ti,
2Mg)−27Ce/Al2O3を得た。これに、ジニト
ジアンミンPt硝酸溶液と硝酸ロジウム(硝酸Rh)溶液
の混合溶液を含浸し、乾燥後450℃で1時間焼成し
た。さらに硝酸Mg溶液を含浸し450℃で1時間焼成
した。以上によりアルミナ(Al2O3)にCe,Mg,N
a,Ti,Rh,Ptを担持したSOx捕捉材、2Mg
−(0.2Rh,2.7Pt)−(18Na,4Ti,2M
g)−27Ce/Al2O3を得た。In the same manner as in T-1, (18Na, 4Ti,
2 mg) was obtained -27Ce / Al 2 O 3. This was impregnated with a mixed solution of a dinitodiamine Pt nitric acid solution and a rhodium nitrate (Rh nitrate) solution, dried, and baked at 450 ° C. for 1 hour. Further, it was impregnated with a Mg nitrate solution and fired at 450 ° C. for 1 hour. By the above, Ce, Mg, N is added to alumina (Al 2 O 3 ).
SOx trapping material supporting a, Ti, Rh, Pt, 2Mg
-(0.2Rh, 2.7Pt)-(18Na, 4Ti, 2M
It was obtained g) -27Ce / Al 2 O 3 .
【0048】《SOx捕捉材例3》SOx捕捉材T−3
を以下の方法で得た。<< SOx Capture Material Example 3 >> SOx Capture Material T-3
Was obtained in the following manner.
【0049】先ず、SOx捕捉材T−1で示した方法で
アルミナコートハニカムを得た。該アルミナコートハニ
カムに硝酸セリウム(硝酸Ce)溶液を含浸し乾燥後6
00℃で1時間焼成した。これに、硝酸パラジウム(硝
酸Pd)溶液を含浸し、乾燥後450℃で1時間焼成し
た。さらに硝酸Mg溶液を含浸し450℃で1時間焼成
した。以上によりアルミナ(Al2O3)にCe,Pd,
Mgを担持したSOx捕捉材、2Mg−3Pd−27C
e/Al2O3を得た。First, an alumina-coated honeycomb was obtained by the method shown for the SOx trap T-1. The alumina coated honeycomb is impregnated with a cerium nitrate (Ce nitrate) solution and dried.
It was baked at 00 ° C. for 1 hour. This was impregnated with a palladium nitrate (Pd nitrate) solution, dried and calcined at 450 ° C. for 1 hour. Further, it was impregnated with a Mg nitrate solution and fired at 450 ° C. for 1 hour. Thus, Ce, Pd, and alumina (Al 2 O 3 )
SOx trapping material supporting Mg, 2Mg-3Pd-27C
e / Al 2 O 3 was obtained.
【0050】[リーンNOx触媒]本発明の方法による
リーンNOx触媒N−1の調製例を示す。[Lean NOx Catalyst] An example of preparing a lean NOx catalyst N-1 according to the method of the present invention will be described.
【0051】上記SOx捕捉材の場合と同じ方法でアル
ミナコートハニカムを得た。該アルミナコートハニカム
に、硝酸セリウム(硝酸Ce)溶液を含浸し乾燥後60
0℃で1時間焼成した。続いて硝酸ナトリウム(硝酸N
a)溶液とチタニアゾル溶液と硝酸マグネシウム(硝酸
Mg)溶液の混合溶液を含浸し、同様に乾燥,焼成し
た。さらにジニトジアンミンPt硝酸溶液と硝酸ロジウ
ム(硝酸Rh)溶液の混合溶液に含浸し、乾燥後450
℃で1時間焼成した。最後に硝酸Mg溶液を含浸し45
0℃で1時間焼成した。以上によりアルミナ(Al
2O3)にCe,Mg,Na,Ti,Rh,Ptを担持し
たハニカム状リーンNOx触媒、2Mg−(0.2Rh,
2.7Pt)−(18Na,4Ti,2Mg)−27Ce/
Al2O3を得た。An alumina-coated honeycomb was obtained in the same manner as in the case of the SOx trapping material. The alumina coated honeycomb is impregnated with a cerium nitrate (Ce nitrate) solution, dried and dried.
It was baked at 0 ° C. for 1 hour. Subsequently, sodium nitrate (nitrate N
a) A mixed solution of a solution, a titania sol solution, and a magnesium nitrate (Mg nitrate) solution was impregnated, and dried and fired similarly. Further, it is impregnated with a mixed solution of a dinitodiamine Pt nitric acid solution and a rhodium nitrate (Rh nitrate) solution, dried, and dried.
Calcination was carried out at ℃ for 1 hour. Finally, impregnate with Mg nitrate solution 45
It was baked at 0 ° C. for 1 hour. As described above, alumina (Al
2 O 3) to Ce, Mg, Na, Ti, Rh, honeycomb lean NOx catalyst carrying Pt, 2Mg- (0.2Rh,
2.7Pt)-(18Na, 4Ti, 2Mg) -27Ce /
Al 2 O 3 was obtained.
【0052】「試験例1」以下、具体的試験例を挙げて
本発明の効果を説明する。Test Example 1 The effects of the present invention will be described below with reference to specific test examples.
【0053】本発明の吸着触媒及び装置の排ガス浄化性
能を評価した。The exhaust gas purification performance of the adsorption catalyst and the device of the present invention was evaluated.
【0054】《試験方法》上記方法で得たSOx捕捉材
及びリーンNOx触媒を用いた排ガス浄化装置の性能
を、以下の方法で評価した。<< Test Method >> The performance of the exhaust gas purifying apparatus using the SOx trapping material and the lean NOx catalyst obtained by the above method was evaluated by the following method.
【0055】排気量1.8L のリーンバーン仕様ガソリ
ンエンジンを搭載した乗用車の排気流路のエンジン直下
に本発明の方法により調製した容積1.0L のハニカム
状(400cell/in2 )のSOx捕捉材を置き、その後
流の床下に容積1.7L のハニカム状(400cell/in
2 )リーンNOx触媒を置いた。SOx捕捉材及びリー
ンNOx触媒は予め700℃で5時間酸化雰囲気で熱処
理し安定化させた。上記の車を、硫黄(S)分を400
ppm 含むガソリンを燃料としシャシダイナモメータ上で
40km/hの定速で走行させた。この間空燃比はA/
F(空気Aと燃料Fの重量費)で22(排ガスは酸化雰
囲気)とし、55秒毎にA/F=13(排ガスは還元雰
囲気)で0.2 秒のリッチ状態を挿入しリーンNOx触
媒のNOx捕捉能を回復させた。走行中、自動車排ガス
測定装置を用いダイレクト分析で排ガス中のNOx濃度
を測定した。尚、以下に掲げるNOx浄化率は、ダイレ
クト分析で得た排ガス組成のリッチ運転挿入直前の値で
代表させた。また試験目的に応じて後述のSOx捕捉材
再生のための排ガスを還元雰囲気とするリッチ運転を行
った。A 1.0-liter honeycomb (400 cell / in 2 ) SOx trapping material prepared by the method of the present invention immediately below an engine in an exhaust passage of a passenger car equipped with a 1.8-liter lean-burn gasoline engine. Was placed under the floor of the flow, and then a honeycomb-shaped honeycomb having a volume of 1.7 L (400 cells / in
2 ) A lean NOx catalyst was placed. The SOx trapping material and the lean NOx catalyst were previously heat-treated in an oxidizing atmosphere at 700 ° C. for 5 hours to be stabilized. The above car, sulfur (S) content 400
The vehicle was driven at a constant speed of 40 km / h on a chassis dynamometer using gasoline containing ppm as fuel. During this time, the air-fuel ratio is A /
F (weight of air A and fuel F) is 22 (exhaust gas is an oxidizing atmosphere), and every 55 seconds, a rich state of A / F = 13 (exhaust gas is a reducing atmosphere) for 0.2 seconds is inserted and lean NOx catalyst The NOx trapping ability was restored. During traveling, the NOx concentration in the exhaust gas was measured by direct analysis using an automobile exhaust gas measuring device. The NOx purification rates listed below were represented by the values of the exhaust gas composition obtained by direct analysis immediately before the insertion of the rich operation. Further, a rich operation was performed in which exhaust gas for regenerating the SOx trapping material described later was used as a reducing atmosphere according to the purpose of the test.
【0056】《試験例1》SOx捕捉材にT−1をリー
ンNOx触媒にN−1を適用した。Test Example 1 T-1 was applied to the SOx trap and N-1 was applied to the lean NOx catalyst.
【0057】40km/hでの走行中、SOx捕捉材入
り口排ガス温度は約450℃であった。また走行10h
毎にA/F=14.5 のリッチ状態で10分間エンジン
回転数を上昇させSOx捕捉材入り口排ガス温度を約6
50℃とした。上記方法で運転を行ったところ運転開始
時にNOx浄化率90%が得られ、100hまではこの
値をほぼ維持した。During traveling at 40 km / h, the temperature of the exhaust gas at the inlet of the SOx trapping material was about 450 ° C. In addition, traveling 10h
Each time, the engine speed was increased for 10 minutes in the rich condition of A / F = 14.5 and the exhaust gas temperature at the inlet of the SOx trapping material was reduced to about 6
50 ° C. When the operation was performed by the above method, a NOx purification rate of 90% was obtained at the start of the operation, and this value was substantially maintained until 100 hours.
【0058】《試験例2》SOx捕捉材にT−2をリー
ンNOx触媒にN−1を適用した。Test Example 2 T-2 was applied to the SOx trap and N-1 was applied to the lean NOx catalyst.
【0059】試験例1と同様の運転を行ったところ運転
開始時にNOx浄化率90%が得られ、100hまでこ
の値をほぼ維持した。When the same operation as in Test Example 1 was performed, a NOx purification rate of 90% was obtained at the start of the operation, and this value was almost maintained until 100 hours.
【0060】《試験例3》SOx捕捉材にT−3をリー
ンNOx触媒にN−1を適用した。Test Example 3 T-3 was applied to the SOx trapping material, and N-1 was applied to the lean NOx catalyst.
【0061】試験例1と同様の運転を行ったが、SOx
捕捉材の再生に当たっては、走行10h毎にA/F=1
4.5 のリッチ状態で10分間エンジン回転数を上昇さ
せSOx捕捉材入り口排ガス温度を約600℃とした。
上記方法で運転を行ったところ運転開始時にNOx浄化
率90%が得られ、100hまでこの値をほぼ維持し
た。The same operation as in Test Example 1 was performed, except that SOx
In regenerating the trapping material, A / F = 1 every 10 hours of running
The engine speed was increased for 10 minutes in the 4.5 rich state, and the exhaust gas temperature at the inlet of the SOx trapping material was set to about 600 ° C.
When the operation was performed by the above method, a NOx purification rate of 90% was obtained at the start of the operation, and this value was almost maintained until 100 hours.
【0062】《試験例4》SOx捕捉材にT−1をリー
ンNOx触媒にN−1を適用した。Test Example 4 T-1 was applied to the SOx trap and N-1 was applied to the lean NOx catalyst.
【0063】試験例3と同様の方法で運転を行ったとこ
ろ、運転開始時にNOx浄化率90%が得られたが、1
00h後に80%にまで低下した。この時点で、A/F
=14.5 のリッチ状態で10分間エンジン回転数をさ
らに上昇させリーンNOx触媒入り口排ガス温度を約5
70℃とした。その結果NOx浄化率90%の性能が回
復した。When the operation was carried out in the same manner as in Test Example 3, a NOx purification rate of 90% was obtained at the start of the operation.
After 00h, it decreased to 80%. At this point, A / F
= 14.5, the engine speed was further increased for 10 minutes, and the exhaust gas temperature at the inlet of the lean NOx catalyst was reduced to about 5
70 ° C. As a result, the performance with a NOx purification rate of 90% was restored.
【0064】《比較例1》SOx捕捉材を設けずリーン
NOx触媒N−1のみを床下に置いた。試験例1と同様
の運転とSOx捕捉材がある場合の再生操作を行った。
運転開始時にはNOx浄化率90%が得られたが20h
後には60%にまで低下した。Comparative Example 1 Only the lean NOx catalyst N-1 was placed under the floor without providing any SOx trapping material. The same operation as in Test Example 1 and a regeneration operation in the case where the SOx trapping material was present were performed.
At the start of operation, a NOx purification rate of 90% was obtained, but 20h
Later it dropped to 60%.
【0065】[0065]
【発明の効果】以上から明らかな様に、本発明の装置に
よれば、排ガス流路にSOx捕捉材を設け、その後流に
リーンNOx触媒を設けることにより、リーンNOx触
媒のSOx被毒を防止しつつ、リーンバーン排ガス中の
NOx等を効果的に浄化できる。As is apparent from the above, according to the apparatus of the present invention, the SOx trapping material is provided in the exhaust gas flow path, and the lean NOx catalyst is provided downstream of the exhaust gas flow path, thereby preventing SOx poisoning of the lean NOx catalyst. In addition, NOx and the like in the lean burn exhaust gas can be effectively purified.
【図1】本発明の代表的な実施態様を示す排ガス浄化装
置の構成図。FIG. 1 is a configuration diagram of an exhaust gas purifying apparatus showing a typical embodiment of the present invention.
1…エアクリーナ、2…エアフローセンサー、3…スロ
ットルバルブ、5…インジェクタ、6…点火プラグ、7
…アクセルペダル、8…負荷センサー、9…吸気温度セ
ンサー、12…燃料ポンプ、13…燃料タンク、17…
SOx捕捉材、18…リーンNOx触媒、19…酸素セ
ンサー、20…SOx捕捉材温度センサー、21…リー
ンNOx触媒温度センサー、25…ECU、26…ノッ
クセンサー、28…水温センサー、29…クランク角セ
ンサー、99…エンジン。DESCRIPTION OF SYMBOLS 1 ... Air cleaner, 2 ... Air flow sensor, 3 ... Throttle valve, 5 ... Injector, 6 ... Spark plug, 7
... Accelerator pedal, 8 ... Load sensor, 9 ... Intake air temperature sensor, 12 ... Fuel pump, 13 ... Fuel tank, 17 ...
SOx trapping material, 18 lean NOx catalyst, 19 oxygen sensor, 20 SOx trapping temperature sensor, 21 lean NOx catalyst temperature sensor, 25 ECU, 26 knock sensor, 28 water temperature sensor, 29 crank angle sensor , 99 ... Engine.
フロントページの続き (72)発明者 奥出 幸二郎 茨城県日立市大みか町七丁目1番1号 株 式会社日立製作所日立研究所内 (72)発明者 小川 敏雄 茨城県日立市大みか町七丁目1番1号 株 式会社日立製作所日立研究所内 (72)発明者 藤谷 守男 茨城県日立市大みか町七丁目1番1号 株 式会社日立製作所日立研究所内 (72)発明者 山下 寿生 茨城県日立市大みか町七丁目1番1号 株 式会社日立製作所日立研究所内 (72)発明者 小豆畑 茂 茨城県日立市大みか町七丁目1番1号 株 式会社日立製作所日立研究所内 (72)発明者 北原 雄一 茨城県ひたちなか市大字高場2520番地 株 式会社日立製作所自動車機器事業部内 (72)発明者 平塚 俊史 茨城県ひたちなか市大字高場2520番地 株 式会社日立製作所自動車機器事業部内 (72)発明者 篠塚 教広 茨城県ひたちなか市大字高場2520番地 株 式会社日立製作所自動車機器事業部内Continuing on the front page (72) Inventor Kojiro Okude 7-1-1, Omika-cho, Hitachi City, Ibaraki Prefecture Inside Hitachi Research Laboratory, Hitachi, Ltd. (72) Inventor Toshio Ogawa 7-1-1, Omika-cho, Hitachi City, Ibaraki Prefecture No. Hitachi, Ltd.Hitachi Research Laboratories (72) Inventor Morio Fujitani 1-1-1, Omikacho, Hitachi City, Ibaraki Prefecture Within Hitachi Research Laboratory, Hitachi Research Laboratories (72) Inventor Hisao Yamashita, Omikamachi, Hitachi City, Ibaraki Prefecture Hitachi 1-1, Hitachi, Ltd., Hitachi Research Laboratories (72) Inventor Shigeru Azuhata 7-1-1, Omika-cho, Hitachi City, Hitachi, Ibaraki Prefecture Hitachi Research Laboratory, Hitachi, Ltd. (72) Inventor Yuichi Kitahara Hitachinaka, Ibaraki 2520 Address, Takahiro-shi, Hitachi, Ltd.Automotive Equipment Division of Hitachi, Ltd. (72) Inventor Toshifumi Hiratsuka 2520 Address, Ojitaka-Oita, Hitachinaka-shi, Ibaraki Automotive Equipment Division of Hitachi, Ltd. (72) Norihiro Shinozuka, Inventor Hitachinaka If 2520 address Co., Ltd. Hitachi automotive equipment business unit
Claims (6)
を吸着,吸収等の方法により捕捉し、捕捉した温度より
高い温度でかつ排ガスに含まれる酸化剤と還元剤の酸化
還元化学量論関係において酸化剤に対し還元剤が同量以
上(還元雰囲気)の場合に捕捉したSOxを脱着あるい
は放出するSOx捕捉材を設け、その後流に、排ガスに
含まれる酸化剤と還元剤の酸化還元化学量論関係におい
て還元剤に対して酸化剤が多い(酸化雰囲気)場合に排
ガス中の炭化水素(HC)と一酸化炭素(CO)を酸化浄
化すると同時にNOxを吸着,吸収等の方法で捕捉し、
還元雰囲気において捕捉したNOxを接触還元してNO
x捕捉能を回復すると同時に排ガス中のNOxの還元浄
化とHC(炭化水素),CO(一酸化炭素)の酸化浄化
を行うリーンNOx触媒を設け、還元雰囲気下でSOx
捕捉材を昇温してSOx捕捉能を回復させることを特徴
とする排ガス浄化装置。An SOx in an exhaust gas is supplied to an exhaust gas passage of an internal combustion engine.
Is trapped by a method such as adsorption or absorption, and at a temperature higher than the trapped temperature and in the redox stoichiometry of the oxidizing agent and the reducing agent contained in the exhaust gas, the reducing agent is equal to or more than the oxidizing agent (reducing atmosphere) In the case of (1), an SOx trapping material for desorbing or releasing the trapped SOx is provided, and in the subsequent stream, the amount of the oxidizing agent is larger than that of the reducing agent in the oxidation-reduction stoichiometry of the oxidizing agent and the reducing agent contained in the exhaust gas (oxidizing atmosphere ) In this case, hydrocarbons (HC) and carbon monoxide (CO) in the exhaust gas are oxidized and purified, and at the same time, NOx is captured by a method such as adsorption and absorption.
NOx trapped in a reducing atmosphere is catalytically reduced to NO
At the same time as recovering the x trapping ability, a lean NOx catalyst for reducing and purifying NOx in exhaust gas and oxidizing and purifying HC (hydrocarbon) and CO (carbon monoxide) is provided.
An exhaust gas purifying apparatus characterized in that the temperature of the trapping material is raised to recover the SOx trapping ability.
捕捉材を昇温してSOx捕捉能を回復させるにあたり、
同時に、還元雰囲気下でリーンNOx触媒を昇温してリ
ーンNOx触媒のSO2 被毒を防止および/またはSO
2 被毒したリーンNOx触媒のNOx捕捉能の再生を図
ることを特徴とする排ガス浄化装置。2. The method according to claim 1, wherein the SOx
In recovering the SOx trapping ability by raising the temperature of the trapping material,
At the same time, the lean NOx catalyst is heated in a reducing atmosphere to prevent SO 2 poisoning of the lean NOx catalyst and / or
(2) An exhaust gas purifying apparatus characterized by regenerating the NOx trapping ability of a poisoned lean NOx catalyst.
が、リチウム(Li),カリウム(K),ナトリウム(N
a)等のアルカリ金属、及びマグネシウム(Mg),カ
ルシウム(Ca),ストロンチウム(Sr),バリウム
(Ba)等のアルカリ土類金属、及びチタン(Ti)、
及びアルミニウム(Al)、及びバナジウム(V),ク
ロム(Cr),マンガン(Mn),鉄(Fe),コバル
ト(Co),ニッケル(Ni),銅(Cu),亜鉛(Z
n)等の第一遷移元素、及びランタン(La),セリウ
ム(Ce)等の希土類金属から選ばれる少なくとも一種
の元素を含む金属酸化物(もしくは複合酸化物)からな
る組成物、該組成物を多孔質耐熱性金属酸化物に担持し
てなる組成物、である排ガス浄化装置。3. The method according to claim 1, wherein the SOx trapping material comprises lithium (Li), potassium (K), sodium (N
a) and alkaline earth metals such as magnesium (Mg), calcium (Ca), strontium (Sr) and barium (Ba), and titanium (Ti);
And aluminum (Al), and vanadium (V), chromium (Cr), manganese (Mn), iron (Fe), cobalt (Co), nickel (Ni), copper (Cu), zinc (Z
a composition comprising a metal oxide (or composite oxide) containing a first transition element such as n) and at least one element selected from rare earth metals such as lanthanum (La) and cerium (Ce); An exhaust gas purifying apparatus, which is a composition supported on a porous heat-resistant metal oxide.
が、リチウム(Li),カリウム(K),ナトリウム(N
a)等のアルカリ金属、及びマグネシウム(Mg),カ
ルシウム(Ca),ストロンチウム(Sr),バリウム
(Ba)等のアルカリ土類金属、及びチタン(Ti)、
及びアルミニウム(Al)、及びバナジウム(V),ク
ロム(Cr),マンガン(Mn),鉄(Fe),コバル
ト(Co),ニッケル(Ni),銅(Cu),亜鉛(Z
n)等の第一遷移元素、及びランタン(La),セリウ
ム(Ce)等の希土類金属から選ばれる少なくとも一種
の元素と、白金(Pt),ロジウム(Rh),パラヂウ
ム(Pd)等の白金族金属(いわゆる貴金属)から選ば
れる少なくとも1種の元素、を含む金属および金属酸化
物(もしくは複合酸化物)からなる組成物、該組成物を
多孔質耐熱性金属酸化物に担持してなる組成物、である
排ガス浄化装置。4. The SOx trap according to claim 1, wherein the SOx trapping material is lithium (Li), potassium (K), sodium (N
a) and alkaline earth metals such as magnesium (Mg), calcium (Ca), strontium (Sr) and barium (Ba), and titanium (Ti);
And aluminum (Al), and vanadium (V), chromium (Cr), manganese (Mn), iron (Fe), cobalt (Co), nickel (Ni), copper (Cu), zinc (Z
n) and at least one element selected from rare earth metals such as lanthanum (La) and cerium (Ce), and a platinum group such as platinum (Pt), rhodium (Rh) and palladium (Pd). Composition comprising metal and metal oxide (or composite oxide) containing at least one element selected from metals (so-called noble metals), composition comprising the composition supported on porous heat-resistant metal oxide , Which is an exhaust gas purification device.
ミニウム(Al)、及びバナジウム(V),クロム(C
r),マンガン(Mn),鉄(Fe),コバルト(C
o),ニッケル(Ni),銅(Cu),亜鉛(Zn)等
の第一遷移元素、及びランタン(La),セリウム(C
e)等の希土類金属、から選ばれる少なくとも一種の元
素と、白金(Pt),ロジウム(Rh),パラヂウム
(Pd)等の貴金属から選ばれる少なくとも1種の元
素、を含む金属および金属酸化物(もしくは複合酸化
物)からなる組成物、該組成物を多孔質耐熱性金属酸化
物に担持してなる組成物、である排ガス浄化装置。5. The method according to claim 4, wherein the SOx trapping material is aluminum (Al), vanadium (V), chromium (C
r), manganese (Mn), iron (Fe), cobalt (C
o), first transition elements such as nickel (Ni), copper (Cu), zinc (Zn), lanthanum (La), cerium (C
and metal oxides containing at least one element selected from rare earth metals such as e) and at least one element selected from noble metals such as platinum (Pt), rhodium (Rh) and palladium (Pd). Or a composite oxide), or a composition obtained by supporting the composition on a porous heat-resistant metal oxide.
媒が、リチウム(Li),ナトリウム(Na),カリウ
ム(K),マグネシウム(Mg),ストロンチウム(S
r),バリウム(Ba)及びカルシウム(Ca)から選
ばれる少なくとも一種と、セリウム(Ce)等からなる
希土類から選ばれる少なくとも一種と、白金(Pt),
ロジウム(Rh),パラヂウム(Pd)等の貴金属から
選ばれる少なくとも一種の元素を含み、必要に応じてシ
リカ(Si),チタン(Ti),ジルコニウム(Zr)
から選ばれる少なくとも一種の元素を含む、金属および
金属酸化物(もしくは複合酸化物)からなる組成物、該
組成物を多孔質耐熱性金属酸化物に担持してなる組成
物、である排ガス浄化装置。6. The method according to claim 1, wherein the lean NOx catalyst comprises lithium (Li), sodium (Na), potassium (K), magnesium (Mg), strontium (S).
r), at least one selected from barium (Ba) and calcium (Ca), at least one selected from rare earths such as cerium (Ce), and platinum (Pt),
Contains at least one element selected from noble metals such as rhodium (Rh) and palladium (Pd), and contains silica (Si), titanium (Ti), and zirconium (Zr) as required.
An exhaust gas purifying apparatus comprising: a composition comprising a metal and a metal oxide (or a composite oxide) containing at least one element selected from the group consisting of: and a composition comprising the composition supported on a porous heat-resistant metal oxide. .
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9239270A JPH1181988A (en) | 1997-09-04 | 1997-09-04 | Exhaust emission control device for internal combustion engine |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9239270A JPH1181988A (en) | 1997-09-04 | 1997-09-04 | Exhaust emission control device for internal combustion engine |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH1181988A true JPH1181988A (en) | 1999-03-26 |
Family
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Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP9239270A Pending JPH1181988A (en) | 1997-09-04 | 1997-09-04 | Exhaust emission control device for internal combustion engine |
Country Status (1)
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JP (1) | JPH1181988A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2841935A1 (en) * | 2002-07-02 | 2004-01-09 | Toyota Motor Co Ltd | EXHAUST GAS PURIFICATION DEVICE FOR AN ENGINE |
JP2008151057A (en) * | 2006-12-19 | 2008-07-03 | Babcock Hitachi Kk | Exhaust emission control method and device for internal combustion engine |
JP2009019552A (en) * | 2007-07-11 | 2009-01-29 | Toyota Motor Corp | Sulfur component detector |
JP2009072740A (en) * | 2007-09-25 | 2009-04-09 | Babcock Hitachi Kk | Exhaust emission control method and device for internal combustion engine |
-
1997
- 1997-09-04 JP JP9239270A patent/JPH1181988A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2841935A1 (en) * | 2002-07-02 | 2004-01-09 | Toyota Motor Co Ltd | EXHAUST GAS PURIFICATION DEVICE FOR AN ENGINE |
JP2008151057A (en) * | 2006-12-19 | 2008-07-03 | Babcock Hitachi Kk | Exhaust emission control method and device for internal combustion engine |
JP2009019552A (en) * | 2007-07-11 | 2009-01-29 | Toyota Motor Corp | Sulfur component detector |
JP2009072740A (en) * | 2007-09-25 | 2009-04-09 | Babcock Hitachi Kk | Exhaust emission control method and device for internal combustion engine |
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