JPS5920385B2 - Exhaust gas purification catalyst treated to prevent phosphorus poisoning - Google Patents

Exhaust gas purification catalyst treated to prevent phosphorus poisoning

Info

Publication number
JPS5920385B2
JPS5920385B2 JP53152490A JP15249078A JPS5920385B2 JP S5920385 B2 JPS5920385 B2 JP S5920385B2 JP 53152490 A JP53152490 A JP 53152490A JP 15249078 A JP15249078 A JP 15249078A JP S5920385 B2 JPS5920385 B2 JP S5920385B2
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
zno
combustion ash
gas purification
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.)
Expired
Application number
JP53152490A
Other languages
Japanese (ja)
Other versions
JPS5579046A (en
Inventor
美津男 安野
俊蔵 高須賀
進 沖内
光昭 河上
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mazda Motor Corp
Original Assignee
Toyo Kogyo Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toyo Kogyo Co Ltd filed Critical Toyo Kogyo Co Ltd
Priority to JP53152490A priority Critical patent/JPS5920385B2/en
Publication of JPS5579046A publication Critical patent/JPS5579046A/en
Publication of JPS5920385B2 publication Critical patent/JPS5920385B2/en
Expired legal-status Critical Current

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  • Exhaust Gas After Treatment (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Description

【発明の詳細な説明】 この発明は、自動車エンジンの排ガス浄化用触媒、特に
りん被毒防止処理を施した触媒に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a catalyst for purifying exhaust gas from an automobile engine, and particularly to a catalyst treated to prevent phosphorus poisoning.

自動車のエンジンオイルには、酸化防止剤、摩耗防止剤
としてジアルキルジチオりん酸の金属塩(金属としてZ
nが一般的である)が添加されているが、上記ジチオり
ん酸金属塩は排ガス浄化用の触媒に対して被毒作用をす
ることが知られている。
Automotive engine oil contains metal salts of dialkyldithiophosphates (as metals) as antioxidants and anti-wear agents.
However, it is known that the above-mentioned metal dithiophosphates have a poisoning effect on catalysts for purifying exhaust gas.

この被毒作用は、上記ジチオりん酸亜鉛がエンジン内で
熱焼してりん酸亜鉛Zn(PO3)2の燃焼灰を生成し
、この燃焼灰がエンジン排気系に設けた排ガス浄化用触
媒の表面に付着し、この付着した熱焼灰が触媒作用によ
る高熱のためにガラス化して触媒表面を被覆して触媒と
排ガスとの接触を妨げ、その結果、排ガス浄化性能を著
しく低減させることによるものである。
This poisoning effect is caused by the above-mentioned zinc dithiophosphate being burned in the engine to produce combustion ash of zinc phosphate, Zn(PO3)2, and this combustion ash is generated on the surface of the exhaust gas purification catalyst installed in the engine exhaust system. This is due to the fact that the adhering burnt ash vitrifies due to the high heat caused by the catalytic action and coats the catalyst surface, preventing contact between the catalyst and exhaust gas, and as a result, the exhaust gas purification performance is significantly reduced. be.

本発明者らは、上記燃焼灰のガラス化について検討した
ところ、ガラス化現象は燃焼灰が加熱される温度によっ
て左右されることを知ったのである。
The present inventors studied the vitrification of the combustion ash and found that the vitrification phenomenon is influenced by the temperature at which the combustion ash is heated.

すなわち上記ジアルキルジチオりん酸亜鉛を2時間加熱
したとき、加熱温度600°Cでは燃焼灰は海綿状であ
り、800℃では一部がガラス化されているが、900
℃では完全にガラス化されている。
That is, when the above zinc dialkyldithiophosphate is heated for 2 hours, the combustion ash is spongy at a heating temperature of 600°C, and is partially vitrified at 800°C;
It is completely vitrified at ℃.

このように燃焼灰が高熱によってガラス化されるのは、
燃焼灰(りん酸亜鉛)中におけるZnO成分とP2O5
成分とのモル比が一定範囲内にあるからである。
The combustion ash is vitrified by high heat in this way.
ZnO component and P2O5 in combustion ash (zinc phosphate)
This is because the molar ratio with the components is within a certain range.

そして種々の研究の結果、上記燃焼灰の生成過程におけ
る高温下でP2O5のモル比がZnO等の金属酸化物に
対しである限度以下になると高熱によるもガラス化しな
いことを知り、この発明を完成するに至ったのである。
As a result of various studies, he learned that if the molar ratio of P2O5 to metal oxides such as ZnO is below a certain limit under high temperatures during the combustion ash generation process, vitrification will not occur even under high heat, and he completed this invention. That's what I came to do.

すなわちこの発明は、エンジンの排ガス用触媒において
、排ガス中に含まれ、触媒表面に付着される燃焼灰のP
2O5とカラス化阻止性金属酸化物であるZnOとの量
的比率が燃焼灰のガラス化し得る範囲を越えて過多とな
る量の触媒11当り1〜loogのZnOを、あらかじ
め触媒表面に被覆したことを特徴とするりん被毒防止処
理を施した排ガス浄化用触媒である。
That is, the present invention provides a catalyst for engine exhaust gas, in which P of combustion ash contained in the exhaust gas and attached to the catalyst surface is reduced.
The surface of the catalyst is coated with ZnO in an amount of 1~loog per 11 catalysts in an amount such that the quantitative ratio of 2O5 and ZnO, which is a vitrification-inhibiting metal oxide, exceeds the range in which combustion ash can be vitrified. This is an exhaust gas purification catalyst that has been treated to prevent phosphorus poisoning.

エンジンの運転によって触媒表面に付着される燃焼灰の
カラス化し得るP2O5とガラス化阻止性金属酸化物で
あるZnOとの最低比率は、ZnO+P2O5に対する
P2O,の量は36モル%である。
The minimum ratio of P2O5, which can form glass in the combustion ash deposited on the catalyst surface during engine operation, and ZnO, which is a vitrification-inhibiting metal oxide, is 36 mol% of P2O to ZnO+P2O5.

ガラス化阻止性金属酸化物としては、ZnOのほかにC
aO,MgO,BaOなどのアルカリ士金属の酸化物が
あげられるが、燃焼灰中にはZn成分を含んでいるため
にZnOの力が燃焼灰とのなじみがよく、ZnOのりん
被毒防止効果は上記アルカリ士金属の酸化物よりも優れ
ている。
In addition to ZnO, C
Examples include oxides of alkali metals such as aO, MgO, and BaO, but since the combustion ash contains Zn components, the power of ZnO blends well with the combustion ash, and ZnO has a phosphorus poisoning prevention effect. is superior to the above-mentioned alkali metal oxides.

エンジンの排ガス浄化作用をする触媒としては、白金、
ロジウム等の貴金属をモノリス担体に付着させるか、ま
たはペレット状としたものが使用されている。
Platinum,
Noble metals such as rhodium are attached to a monolithic carrier or are used in the form of pellets.

そして触媒には、排ガス中に含有している炭化水素、一
酸化炭素などの還元物質を酸化燃焼させる酸化触媒と、
上記酸化作用のほかに、排ガス中に含まれているNOx
を還元させる酸化還元触媒とが使用されている。
The catalyst includes an oxidation catalyst that oxidizes and burns reducing substances such as hydrocarbons and carbon monoxide contained in exhaust gas,
In addition to the above oxidation effect, NOx contained in exhaust gas
A redox catalyst is used to reduce the oxidation-reduction catalyst.

上記ジチオりん酸金属塩の燃焼灰が触媒に対して被毒作
用をする量は、触媒の種類、触媒の形態によって相違す
るので、この発明を実施するためには、あらかじめ触媒
の浄化作用が被毒によって低下するに至る際のりん成分
付着量を測定し、そのりん成分付着量に相当して上記の
燃焼灰がガラス化し得るP2O5とZnOの最低比率以
上になるようにZnOをあらかじめ触媒に付着させてお
くのである。
The amount of the combustion ash of the metal dithiophosphate that poisons the catalyst varies depending on the type and form of the catalyst. Measure the amount of phosphorus component attached when the amount of phosphorus component decreases due to poisoning, and attach ZnO to the catalyst in advance so that the above-mentioned combustion ash becomes the minimum ratio of P2O5 and ZnO that can be vitrified, corresponding to the amount of phosphorus component attached. Let it be.

ZnOの付着量は、触媒ll当り1〜100g、好まし
くは1〜30gである。
The amount of ZnO deposited is 1 to 100 g, preferably 1 to 30 g per liter of catalyst.

なお、上記範囲の下限値はりん被毒の影響が出始める点
をりん0,1重量係付着時とし、また上限値はりん被着
量の上限を実験的に求めてりん2.0重量%としてこれ
を基礎として求めたものである。
The lower limit of the above range assumes that the effect of phosphorus poisoning starts to appear when 0.1% by weight of phosphorus is deposited, and the upper limit of the above range is determined by experimentally determining the upper limit of the amount of phosphorus deposited at 2.0% by weight of phosphorus. This is the basis for the calculation.

上記のZnOの付着量が下限値より小さくなると、りん
被毒が大きい場合に燃焼灰がガラス化する領域となって
被毒現象がおこり、これに反して上限値や越える場合に
は、被毒防止効果が飽和するばかりでなく、ZnOが触
媒の活性表面を覆う量が増大するので好ましくない。
When the amount of ZnO deposited above is smaller than the lower limit, the combustion ash becomes vitrified when the phosphorus poisoning is large, and a poisoning phenomenon occurs; This is not preferable because not only the preventive effect is saturated, but also the amount of ZnO that covers the active surface of the catalyst increases.

上記触媒表面にZnOを付着させるには、触媒は上記金
属の水溶液、たとえば金属硝酸塩もしくは酢酸塩の水溶
液に浸漬したのち乾燥・焼成を行なう。
In order to attach ZnO to the surface of the catalyst, the catalyst is immersed in an aqueous solution of the metal, such as a metal nitrate or acetate, and then dried and fired.

以下にこの発明の詳細な説明する。This invention will be explained in detail below.

実施例 1 コージェライトから成形され、六角形状の穴48個/d
を有する直径25.4励、長さ50段(触媒体積24彪
)のモノリス担体に白金を1.6E//lの割合で付着
させ、更にこの触媒を硝酸亜鉛水溶液に浸漬、焼成して
、表面にZn052971の割合に被覆した触媒を作成
した。
Example 1 Molded from cordierite, 48 hexagonal holes/d
Platinum was deposited on a monolithic carrier having a diameter of 25.4 mm and a length of 50 stages (catalyst volume of 24 mm) at a rate of 1.6 E//l, and the catalyst was further immersed in an aqueous zinc nitrate solution and fired. A catalyst was prepared whose surface was coated with Zn052971.

この触媒を市販のアルキルジチオりん酸亜鉛1と灯油4
との混合液に浸漬したのち、700℃、20分間炉内に
放置し、更に空冷する操作を16回繰返して、触媒ll
当りZn(PO3)z99.6 gをもってりん被毒し
た触媒試料を作成した。
This catalyst was mixed with 1 part of commercially available zinc alkyl dithiophosphate and 4 parts of kerosene.
After immersing the catalyst in a mixed solution of
A phosphorus-poisoned catalyst sample was prepared using 99.6 g of Zn(PO3) per sample.

この触媒試料に対して、空燃比16.Oの混合気を燃焼
して得た排ガスを、カス流量161/分、空間速度40
,000時間で通過させて炭化水素に対する浄化率を測
定″した。
For this catalyst sample, the air/fuel ratio was 16. The exhaust gas obtained by burning the O mixture is heated at a gas flow rate of 161/min and a space velocity of 40
,000 hours, and the purification rate for hydrocarbons was measured.

一力、比較のために、ZnO被覆をしない触媒を使用し
て上記と同様に浄化率を測定した。
For comparison, the purification rate was measured in the same manner as above using a catalyst not coated with ZnO.

上記の測定結果を第1図のグラフで示した。The above measurement results are shown in the graph of FIG.

上記第1図のグラフで分かるように、ZnO被覆した触
媒A(実線)は、Z r]O被覆しない触媒B(点線)
に比べて、りん被毒前において若干高温にならなければ
浄化率は向上しないが、りん被毒に対する浄化効果は優
れ、浄化効率の低下が少ない。
As can be seen from the graph in Figure 1 above, catalyst A coated with ZnO (solid line) is different from catalyst B coated with Zr]O (dotted line).
Compared to , the purification rate does not improve unless the temperature is slightly higher before phosphorus poisoning, but the purification effect against phosphorus poisoning is excellent and there is little decrease in purification efficiency.

実施例 2 上記実施例1においてモノリス担体に白金の代わりに白
金10、ロジウム1の割合の混合物を129/lの割合
で付着した酸化還元触媒を使用した以外は、実施例1と
同様にして浄化率を測定し、その結果を第2図のグラフ
で示した。
Example 2 Purification was carried out in the same manner as in Example 1, except that instead of platinum in Example 1, a redox catalyst having a mixture of 10 parts platinum and 1 part rhodium attached at a ratio of 129/l was used on the monolithic carrier. The ratio was measured and the results are shown in the graph of FIG.

第2図のグラフで分かるように第1図と同様な傾向の浄
化作用が得られる。
As can be seen from the graph in FIG. 2, a purifying effect having the same tendency as in FIG. 1 can be obtained.

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

第1図は実施例1の触媒入口温度とHC浄化率との関係
を示すグラフ、第2図は実施例2の触媒入口温度とHC
浄化率との関係を示すグラフであり、上記グラフの実線
A、aはZnO被覆した触媒、点線B、bはZnO被覆
しない触媒にして、A、Bはりん被毒前、a、bはりん
被毒後を示している。
Figure 1 is a graph showing the relationship between catalyst inlet temperature and HC purification rate in Example 1, and Figure 2 is a graph showing the relationship between catalyst inlet temperature and HC purification rate in Example 2.
This is a graph showing the relationship with the purification rate. In the above graph, solid lines A and a are for catalysts coated with ZnO, dotted lines B and b are for catalysts that are not coated with ZnO, A and B are before phosphorus poisoning, and a and b are for catalysts coated with phosphorus. It shows after being poisoned.

Claims (1)

【特許請求の範囲】[Claims] 1 エンジンの排ガス浄化用触媒において、排ガス中に
含まれ触媒表面に付着される燃焼灰のP2O5とガラス
化阻止性金属酸化物であるZnOとの量的比率が燃焼灰
のガラス化し得る範囲を越えて過多となる量の触媒ll
当り1〜100.!i’のZnOを、あらかじめ触媒表
面に被覆したことを特徴とするりん被毒防止処理を施し
た排ガス浄化用触媒。
1. In a catalyst for purifying engine exhaust gas, the quantitative ratio of P2O5 in the combustion ash contained in the exhaust gas and attached to the catalyst surface to ZnO, which is a vitrification-inhibiting metal oxide, exceeds the range in which the combustion ash can be vitrified. Excessive amount of catalyst
1-100 per hit. ! An exhaust gas purifying catalyst subjected to phosphorus poisoning prevention treatment, characterized in that the catalyst surface is coated with i' ZnO in advance.
JP53152490A 1978-12-09 1978-12-09 Exhaust gas purification catalyst treated to prevent phosphorus poisoning Expired JPS5920385B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53152490A JPS5920385B2 (en) 1978-12-09 1978-12-09 Exhaust gas purification catalyst treated to prevent phosphorus poisoning

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53152490A JPS5920385B2 (en) 1978-12-09 1978-12-09 Exhaust gas purification catalyst treated to prevent phosphorus poisoning

Publications (2)

Publication Number Publication Date
JPS5579046A JPS5579046A (en) 1980-06-14
JPS5920385B2 true JPS5920385B2 (en) 1984-05-12

Family

ID=15541604

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53152490A Expired JPS5920385B2 (en) 1978-12-09 1978-12-09 Exhaust gas purification catalyst treated to prevent phosphorus poisoning

Country Status (1)

Country Link
JP (1) JPS5920385B2 (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2897367B2 (en) * 1990-01-12 1999-05-31 日本特殊陶業株式会社 Poisoning prevention body, catalyst with poisoning prevention layer, and exhaust gas purification device
US6727097B2 (en) * 2000-06-15 2004-04-27 Engelhard Corporation Method and apparatus for accelerated catalyst poisoning and deactivation
JP4617620B2 (en) * 2001-08-03 2011-01-26 マツダ株式会社 Catalyst for oxidizing exhaust gas containing phosphorus, and exhaust gas oxidizer
SE0203317L (en) * 2002-11-11 2004-05-12 Perstorp Formox Ab Catalyst for catalytic oxidation of hydrocarbons
US7743738B2 (en) * 2007-03-01 2010-06-29 Afton Chemical Corporation Scavenging phosphorus, sulfur, and lead from combustion exhaust using tungsten compounds and lubricant
JP5504834B2 (en) * 2009-11-13 2014-05-28 トヨタ自動車株式会社 Exhaust gas purification catalyst

Also Published As

Publication number Publication date
JPS5579046A (en) 1980-06-14

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