JPH05208816A - Production of cerium hydroxide and cerium oxide - Google Patents

Production of cerium hydroxide and cerium oxide

Info

Publication number
JPH05208816A
JPH05208816A JP4037261A JP3726192A JPH05208816A JP H05208816 A JPH05208816 A JP H05208816A JP 4037261 A JP4037261 A JP 4037261A JP 3726192 A JP3726192 A JP 3726192A JP H05208816 A JPH05208816 A JP H05208816A
Authority
JP
Japan
Prior art keywords
cerium
aqueous solution
hydroxide
cerium hydroxide
alkali
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
Application number
JP4037261A
Other languages
Japanese (ja)
Inventor
Makoto Nakamura
良 中村
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.)
Sumitomo Metal Mining Co Ltd
Original Assignee
Sumitomo Metal Mining 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 Sumitomo Metal Mining Co Ltd filed Critical Sumitomo Metal Mining Co Ltd
Priority to JP4037261A priority Critical patent/JPH05208816A/en
Publication of JPH05208816A publication Critical patent/JPH05208816A/en
Pending legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F17/00Compounds of rare earth metals
    • C01F17/20Compounds containing only rare earth metals as the metal element
    • C01F17/206Compounds containing only rare earth metals as the metal element oxide or hydroxide being the only anion
    • C01F17/224Oxides or hydroxides of lanthanides
    • C01F17/235Cerium oxides or hydroxides

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Inorganic Chemistry (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Catalysts (AREA)

Abstract

PURPOSE:To provide a producing method of cerium hydroxide and cerium oxide small in crystal diameter of cerium oxide finally obtained and capable of giving a catalyst larger in oxygen occluding ability than a conventional catalyst and capable of carrying in good dispersibility on a support. CONSTITUTION:When an alkali is added to an aqueous solution of cerium (IV) sulfate and cerium oxide is precipitated by hydrolysis with the alkali, an aqueous solution of the alkali is dropwise added to an aqueous solution of cerium (IV) sulfate, but the addition is temporarily stopped until cerium hydroxide once produced is re-dissolved in the aqueous solution of cerium sulfate, and after cerium hydroxide is completely re-dissolved, addition of the aqueous solution of alkali is again carried out. The reaction for depositing cerium hydroxide is finished so that pH of the reaction liquid in a state where the produced cerium hydroxide is not dissolved may be <=2.0 and the deposited cerium hydroxide is washed, dried and burned to produce the objective cerium oxide.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、排ガス、特に自動車の
排ガスの浄化触媒に助触媒として用いられる水酸化セリ
ウム及び酸化セリウムに関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to cerium hydroxide and cerium oxide used as a cocatalyst for purifying exhaust gas, particularly automobile exhaust gas.

【0002】[0002]

【従来の技術】排ガス中のCO、HC、Noxの3成分
を同時に浄化するために、Pt、Pd、Rdなどの触媒
金属が用いられている。これら触媒の性能を助長するた
めに従来はNiが添加されていたが、最近ではNiより
もCeO2がよい性能が得られると「触媒」1989年
第31巻566〜571ページに報告されている。触媒
上のCeO2は酸素貯蔵効果、水性ガスシフト反応促進
効果、貴金属の分散性向上効果、担体の高温耐熱性向上
効果を有するとされている。
2. Description of the Related Art Catalytic metals such as Pt, Pd and Rd are used to purify three components of CO, HC and Nox in exhaust gas at the same time. Although Ni was conventionally added to promote the performance of these catalysts, it has recently been reported in "Catalyst" 1989, Vol. 31, pp. 566-571 that CeO 2 has better performance than Ni. . CeO 2 on the catalyst is said to have an oxygen storage effect, a water gas shift reaction promoting effect, a noble metal dispersibility improving effect, and a high temperature heat resistance improving effect of the carrier.

【0003】この報告によれば、触媒上のCeO2の結
晶化は温度の上昇にほぼ比例して進行し、O2吸着量は
800℃を超えると急激に低下する。このCeO2の結
晶子径の成長を押えるためにBaとZrを添加した高温
耐熱用触媒も既に市販されている。浄化性能に大きな関
係を持つのはO2吸着量である。O2吸着量はCeO2
結晶子径が小さいほど大きくなる。従って、焼成された
担体のアルミナ中におけるCeO2の結晶子径が小さい
と、その担体に白金族金属を担持させた触媒は、触媒と
しての性能の向上したものとなる。
According to this report, the crystallization of CeO 2 on the catalyst proceeds almost in proportion to the temperature rise, and the O 2 adsorption amount drops sharply when the temperature exceeds 800 ° C. A high temperature heat resistant catalyst to which Ba and Zr are added in order to suppress the growth of the crystallite diameter of CeO 2 is already on the market. The amount of O 2 adsorption has a great relationship with the purification performance. The smaller the crystallite diameter of CeO 2 , the larger the amount of O 2 adsorbed. Therefore, if the crystallite size of CeO 2 in alumina of the calcined support is small, the catalyst in which the platinum group metal is supported on the support has improved performance as a catalyst.

【0004】触媒担体への酸化セリウムの担持は、セリ
ウム塩の水溶液や、水酸化セリウムをアルミナ等の触媒
担体に付着させ、乾燥焼成するか、あるいはセリウム塩
の水溶液と担体とを混合し、この混合物にアルカリを添
加して、担体上に水酸化セリウムを析出せしめ、これを
乾燥焼成する方法、更にアルミナ粉末と酸化セリウム粉
末とのスラリーを多孔質担体に付着せしめる方法などに
より行われている。セリウム塩の水溶液にアルカリを添
加し水酸化セリウムとする場合には、特開昭56−14
7634号公報、特開昭57−56041号公報、特開
昭57−119835号公報に示されているように、一
般に三価の水溶性セリウム塩を用い、アルカリでpH8
〜11にして水酸化セリウムを生成せしめている。
To support cerium oxide on a catalyst carrier, an aqueous solution of cerium salt or cerium hydroxide is adhered to a catalyst carrier such as alumina and dried or calcined, or an aqueous solution of cerium salt and a carrier are mixed, This is carried out by a method of adding an alkali to the mixture to precipitate cerium hydroxide on the carrier, drying and firing the cerium hydroxide, and a method of attaching a slurry of alumina powder and cerium oxide powder to the porous carrier. When an alkali is added to an aqueous solution of cerium salt to form cerium hydroxide, it is disclosed in JP-A-56-14.
As disclosed in Japanese Patent No. 7634, Japanese Patent Application Laid-Open No. 57-56041, and Japanese Patent Application Laid-Open No. 57-119835, a trivalent water-soluble cerium salt is generally used, and the pH is adjusted to 8 at an alkali.
The cerium hydroxide is made to be -11.

【0005】[0005]

【発明が解決しようとする課題】本発明は、このような
用途に用いて最終的に得られた酸化セリウムの結晶子径
が小さく、従来よりも酸素吸蔵能の大きく、担体へ分散
性よく担持できる触媒を得ることのできる水酸化セリウ
ムおよび酸化セリウムの製造方法を提供することを課題
とする。
DISCLOSURE OF THE INVENTION According to the present invention, the cerium oxide finally obtained for such use has a smaller crystallite size, a larger oxygen storage capacity than before, and a good dispersibility on a carrier. An object of the present invention is to provide a method for producing cerium hydroxide and cerium oxide that can obtain a catalyst that can be obtained.

【0006】[0006]

【課題を解決するための手段】本発明は上記の課題を解
決するため、硫酸第二セリウム水溶液にアルカリ水溶液
を加えて加水分解により水酸化セリウムを沈澱させる
際、硫酸第二セリウム水溶液にアルカリ水溶液を滴下し
一旦生成した水酸化セリウムが硫酸第二セリウム水溶液
に再溶解するまでアルカリ水溶液の滴下を一時中止し、
完全に再溶解させた後再びアルカリ水溶液の添加をする
操作を行い、生成した水酸化セリウムが再溶解しない状
態の反応液のpHが2.0以下で水酸化セリウムを析出
せしめる反応を終了して水酸化セリウムを得ること、及
びこれを洗浄、乾燥、焼成して酸化セリウムとすること
にある。
[Means for Solving the Problems] In order to solve the above problems, the present invention is directed to the addition of an alkaline aqueous solution to a ceric sulfate aqueous solution to precipitate cerium hydroxide by hydrolysis. , And once the cerium hydroxide that was once generated was redissolved in the cerium sulfate aqueous solution, the addition of the alkaline aqueous solution was temporarily stopped,
After completely re-dissolving, the operation of adding an alkaline aqueous solution again is performed, and the reaction for precipitating cerium hydroxide is completed when the pH of the reaction solution in which the produced cerium hydroxide is not re-dissolved is 2.0 or less. The purpose is to obtain cerium hydroxide and to wash, dry, and calcine it to obtain cerium oxide.

【0007】本発明に用いる硫酸第二セリウムとして
は、一般にCe(SO42・4H2Oが用いられる。ア
ルカリとしては、一般にアルカリとして使用されている
水酸化ナトリウム、水酸化カリウム、水酸化カルシウ
ム、水酸化マグネシウム、アンモニア水を用いることが
できる。
Ce (SO 4 ) 2 .4H 2 O is generally used as the ceric sulfate used in the present invention. As the alkali, it is possible to use sodium hydroxide, potassium hydroxide, calcium hydroxide, magnesium hydroxide, or aqueous ammonia which is generally used as an alkali.

【0008】セリウム塩の水溶液としては10〜500
mmol/l、一般的には50〜200mmol/l程
度の濃度が用いられ、これより薄いと生産性が悪くな
り、これより濃いときは、反応の際のpHの調節が困難
となる。アルカリ水溶液としては10〜2000mmo
l/l、セリウム塩水溶液濃度の1〜1000倍程度、
通常1〜10倍程度である。
An aqueous solution of cerium salt is 10 to 500
A concentration of about mmol / l, generally about 50 to 200 mmol / l, is used. If the concentration is lower than this, the productivity deteriorates. If the concentration is higher than this, it becomes difficult to control the pH during the reaction. 10 ~ 2000mmo as alkaline aqueous solution
l / l, about 1 to 1000 times the cerium salt aqueous solution concentration,
It is usually about 1 to 10 times.

【0009】[0009]

【作用】本発明製造方法においては、用意したセリウム
塩水溶液にアルカリ水溶液を滴下して、液温20〜80
℃、通常20〜40℃で、液を激しく撹拌しながら加水
分解反応を行わせるのであるが、この時、セリウム塩水
溶液にアルカリ水溶液を滴下すると、反応液中に微細な
水酸化セリウムの結晶が生成する。結晶の生成した反応
液に続けてアルカリを添加すると、生成した水酸化セリ
ウムが反応液中で均一に分散しないので、生成する水酸
化セリウムの粒度が不均一となり水酸化セリウムの結晶
粒が大きくなり、結局得られた水酸化セリウムを焼成し
て得た酸性セリウムも結晶子径の小さいものが得られな
くなる。これを避けるためにアルカリ水溶液を滴下し一
旦生成した水酸化セリウムが硫酸第二セリウム水溶液に
再溶解するまでアルカリ水溶液の滴下を一時中止し、完
全に再溶解した後アルカリ水溶液を添加する操作を行う
ものである。
In the production method of the present invention, an aqueous alkali solution is added dropwise to the prepared aqueous cerium salt solution to obtain a liquid temperature of 20-80.
The hydrolysis reaction is carried out at ℃, usually 20 to 40 ℃ while vigorously stirring the solution. At this time, when an alkaline aqueous solution is dropped into the cerium salt aqueous solution, fine cerium hydroxide crystals are formed in the reaction solution. To generate. If alkali is added continuously to the reaction solution in which crystals are generated, the generated cerium hydroxide will not be uniformly dispersed in the reaction solution, and the particle size of the generated cerium hydroxide will be uneven and the crystal particles of cerium hydroxide will increase. As a result, it becomes impossible to obtain an acidic cerium having a small crystallite size by calcining the obtained cerium hydroxide. In order to avoid this, the operation of adding the alkaline aqueous solution by temporarily dropping the alkaline aqueous solution until the cerium hydroxide once generated is redissolved in the aqueous cerium sulfate aqueous solution and completely re-dissolved It is a thing.

【0010】この加水分解反応は、反応液のpHをpH
計で監視しながら行う。例えば、硫酸第二セリウム水溶
液のpHは反応開始時には1.0で、アルカリ水溶液を
添加して行くとpHは上昇するが、加えたアルカリ量に
対してその上昇の仕方は一定せず、初めのうちは遅く、
一旦水酸化セリウム結晶が反応液中で安定に存在する中
和点に達すると、pHが急上昇するようになる。このた
めアルカリの添加を徐々に行わないと、反応液のpHを
pH計で監視しながら行っても、pHを急上昇させてし
まう。アルカリの添加速度はセリウム塩水溶液中のセリ
ウム塩1mmolに対して毎分0.1mmol以下、好
ましくは0.01 mmol前後とするのがよい。
In this hydrolysis reaction, the pH of the reaction solution is adjusted to pH.
Perform while monitoring with a meter. For example, the pH of the cerium sulfate aqueous solution is 1.0 at the start of the reaction, and the pH increases with the addition of the alkaline aqueous solution, but the manner of the increase is not constant with respect to the amount of the added alkali. We are late,
Once the neutralization point where the cerium hydroxide crystals are stably present in the reaction solution is reached, the pH suddenly rises. For this reason, if the alkali is not added gradually, the pH of the reaction solution will rise sharply even if it is monitored with a pH meter. The addition rate of alkali is 0.1 mmol / min or less, preferably about 0.01 mmol / min with respect to 1 mmol of cerium salt in the cerium salt aqueous solution.

【0011】硫酸セリウム水溶液を加水分解して水酸化
セリウムが安定に存在するようになるpHは1.4であ
るが、このように出来るだけ低いpHで水酸化セリウム
を安定に存在せしめ、そこで反応を中止することによ
り、これから得られる酸化セリウムの結晶子径を最も小
さくできるようにしたものである。三価のセリウム塩を
使用する従来法と異なり、このように低いpH領域で水
酸化セリウムを生成できる理由は、明らかではないが、
四価のセリウム塩を出発物質として使用することによる
ものと考えられる。
The pH at which cerium hydroxide aqueous solution is hydrolyzed and cerium hydroxide is stably present is 1.4. However, cerium hydroxide is allowed to stably exist at such a low pH as possible and the reaction is carried out there. By stopping the above, the crystallite diameter of cerium oxide obtained from this can be minimized. It is not clear why, unlike the conventional method using a trivalent cerium salt, cerium hydroxide can be produced in such a low pH range,
It is believed that this is due to the use of a tetravalent cerium salt as a starting material.

【0012】本発明で、加水分解時のpHの最高値を
2.0とするのは、pHが2.0を超えて反応を終了する
と、最終的に得られた酸化セリウムの結晶子径が大きく
なり、酸素吸蔵能が低下するからである。その理由は、
pHが2.0を超えると、生成する水酸化セリウムに配
位する水和イオンの数が増加することによると考えられ
る。
In the present invention, the maximum value of pH during hydrolysis is set to 2.0, that is, when the reaction is completed when the pH exceeds 2.0, the crystallite size of the cerium oxide finally obtained is This is because the oxygen storage capacity becomes large and the oxygen storage capacity decreases. The reason is,
It is considered that when the pH exceeds 2.0, the number of hydrated ions coordinated with the generated cerium hydroxide increases.

【0013】得られた水酸化セリウムの沈澱は、遠心濾
過あるいは吸引濾過などの方法により反応母液と分離さ
れる。この操作は、反応物を周囲温度の10〜25℃に
冷却する前又は後でもよい。母液と分離した水酸化セリ
ウムは5〜90℃の蒸留水やイオン交換水で数回洗浄し
て水酸化セリウムに付着している酸性陰イオンを除去
し、大気中あるいは10-2〜100mmHg程度の減圧
下で乾燥し、90〜200℃の温度で10〜48時間乾
燥し、更に300〜500℃で2〜12時間焼成して酸
化セリウムとされる。
The obtained cerium hydroxide precipitate is separated from the reaction mother liquor by a method such as centrifugal filtration or suction filtration. This operation may be before or after cooling the reaction to ambient temperature of 10-25 ° C. The cerium hydroxide separated from the mother liquor is washed several times with distilled water or ion-exchanged water at 5 to 90 ° C to remove the acidic anions adhering to the cerium hydroxide, and the cerium hydroxide is removed from the atmosphere or at a temperature of 10 -2 to 100 mmHg. It is dried under reduced pressure, dried at a temperature of 90 to 200 ° C. for 10 to 48 hours, and further baked at 300 to 500 ° C. for 2 to 12 hours to obtain cerium oxide.

【0014】本発明において、酸化セリウムの結晶子径
Lは、X線回折図における(331)面の線幅からシェ
ラーの式を用いて以下のように計算して求めたものであ
る。 L=Kλ/β・cosθ 但し K=0.9 :Sherrer 定数 λ(Å) :Kα1線の波長 1.54Å β(rad) :ピークの線幅(半値幅) θ :入射角
In the present invention, the crystallite diameter L of cerium oxide is obtained by the following calculation from the line width of the (331) plane in the X-ray diffraction diagram using Scherrer's equation. L = Kλ / β · cos θ where K = 0.9: Sherrer constant λ (Å): Wavelength of Kα1 line 1.54Å β (rad): Peak line width (half width) θ: Incident angle

【0015】また、酸化セリウムの酸素吸蔵能の評価
は、Journal of Catalysis., vol.86,p.254(1984)に記
載されている方法に習って酸化セリウム0.05gに対
して以下のように行った。 1)ヘリウム気流(100ml/min)中500℃で3
0分の前処理をする。 2)ヘリウム気流400℃及び500℃に設定。 3)次に1%O2/Heの気流を10秒間(2.5ml)流
し、次の4分50秒間Heを流すサイクルを、導入した
2が消費されなくなるまで(酸化セリウムがそれ以上
2を吸収しなくなるまで)繰り返す。
Further, the evaluation of the oxygen storage capacity of cerium oxide was carried out according to the method described in Journal of Catalysis., Vol.86, p.254 (1984) with respect to 0.05 g of cerium oxide as follows. Went to. 1) 3 at 500 ° C in helium gas flow (100 ml / min)
Pre-process for 0 minutes. 2) Helium flow set to 400 ℃ and 500 ℃. 3) Next, a cycle of flowing a 1% O 2 / He gas stream for 10 seconds (2.5 ml) and then flowing He for 4 minutes and 50 seconds is continued until the introduced O 2 is no longer consumed (cerium oxide is no more than O Repeat until 2 no longer absorbs).

【0016】4)1%CO/Heの気流を10秒間(5.
0ml)流し、次の4分50秒間Heを流す操作を繰り
返し、COが消費されなくなった(酸化セリウムがそれ
以上COを吸収しなくなった)時点で止める。 5)次に、1%O2/Heの気流を10秒間(2.5ml)
流し、次の4分50秒間Heを流す操作を繰り返し、O
2が消費されなくなった時点で止め、この時の全O2消費
量(積算値モル)を酸化セリウムのモル量で割ってOS
CC(OxygenStorage Capacity Cumulative)を計算す
る。
4) An air flow of 1% CO / He was applied for 10 seconds (5.
0 ml) and then He is flown for the next 4 minutes and 50 seconds, and is stopped when CO is no longer consumed (cerium oxide no longer absorbs CO). 5) Next, air flow of 1% O 2 / He for 10 seconds (2.5 ml)
Repeat the operation of flowing He and flowing He for the next 4 minutes and 50 seconds.
Stop when 2 is no longer consumed, and divide the total O 2 consumption (integrated value mol) at this time by the molar amount of cerium oxide to give the OS.
Calculate CC (Oxygen Storage Capacity Cumulative).

【0017】[0017]

【実施例】【Example】

実施例1 100mmol/l濃度のCe(SO42水溶液1lを
25℃に保ち、この液を激しく撹拌しながら、ビュレッ
トから1mol/l濃度の水酸化ナトリウム水溶液を
1.0ml/minの滴下速度で滴下した。水酸化ナト
リウム水溶液を約40ml滴下した時点で白色微結晶の
水酸化セリウムの生成が認められた。この時点で水酸化
ナトリウム水溶液の滴下を一時中止し、撹拌を続けたと
ころやがて結晶は完全に溶解して消失した。再び水酸化
ナトリウム水溶液の滴下を開始し、水酸化ナトリウム水
溶液180mlを滴下した時点で生成した白色微結晶は
溶解しなくなった。この時のpHは1.4であったが、
更に水酸化ナトリウム水溶液の滴下を続け水酸化ナトリ
ウム水溶液200mlを添加した時点で反応を終了し
た。このときのpHは1.5であった。
Example 1 1 l of an aqueous solution of Ce (SO 4 ) 2 having a concentration of 100 mmol / l was kept at 25 ° C., and the solution was vigorously stirred, and a 1 mol / l aqueous solution of sodium hydroxide was dripped from a buret at a rate of 1.0 ml / min. It was dripped at. When about 40 ml of the aqueous sodium hydroxide solution was added dropwise, formation of white microcrystalline cerium hydroxide was observed. At this point, the dropping of the aqueous sodium hydroxide solution was temporarily stopped, and when stirring was continued, the crystals completely dissolved and disappeared. The dropping of the aqueous sodium hydroxide solution was started again, and the white microcrystals formed when 180 ml of the aqueous sodium hydroxide solution was dropped were not dissolved. The pH at this time was 1.4,
The reaction was terminated at the point of time when 200 ml of the sodium hydroxide aqueous solution was added by continuing the dropwise addition of the sodium hydroxide aqueous solution. The pH at this time was 1.5.

【0018】得られた黄色の沈澱物を濾別し、これを8
0℃のイオン交換水100ml中に分散させて5分間撹
拌分散し濾過する操作を3回繰り返した後、120℃で
12時間乾燥し、更に空気中で900℃で3時間焼成し
て酸化セリウム粉末を得た。この酸化セリウム粉末の結
晶子径は、上記のX線回折図の結果からの計算で400
Åであった。前記の酸化セリウムの酸素吸蔵能の評価法
に従って試験を行った結果、OSCCは400℃で1.
3mmol−O2/mol−CeO2、500℃で5.7
mmol−O2/mol−CeO2であった。
The yellow precipitate obtained was filtered off and washed with 8
Cerium oxide powder was dispersed in 100 ml of 0 ° C. ion-exchanged water, stirred and dispersed for 5 minutes and filtered three times, dried at 120 ° C. for 12 hours, and further calcined in air at 900 ° C. for 3 hours. Got The crystallite diameter of this cerium oxide powder is 400 calculated from the above X-ray diffraction pattern.
It was Å. As a result of a test conducted according to the above-mentioned evaluation method of oxygen storage capacity of cerium oxide, OSCC was 1.
3mmol-O 2 / mol-CeO 2, 5.7 at 500 ° C.
It was mmol-O 2 / mol-CeO 2.

【0019】実施例2 実施例1において、反応終了時点でのpHを1.9とし
た以外は実施例1と同様にして酸化セリウム粉末を得
た。この酸化セリウム粉末の結晶子径を実施例1と同様
に計算して求めた結果410Åであった。また、前記の
酸化セリウムの酸素吸蔵能の評価法に従って試験を行っ
た結果、OSCCは400℃で1.4mmol−O2/m
ol−CeO2、500℃で5.2mmol−O2/mo
l−CeO2であった。
Example 2 A cerium oxide powder was obtained in the same manner as in Example 1 except that the pH at the end of the reaction was 1.9. The crystallite size of this cerium oxide powder was calculated in the same manner as in Example 1 and the result was 410Å. In addition, as a result of performing a test according to the evaluation method of the oxygen storage capacity of cerium oxide, OSCC was 1.4 mmol-O 2 / m at 400 ° C.
ol-CeO 2 , 5.2 mmol-O 2 / mo at 500 ° C.
It was 1-CeO 2 .

【0020】比較例1 実施例1において、反応終了時点でのpHを2.1とし
た以外は実施例1と同様にして酸化セリウム粉末を得
た。この酸化セリウム粉末の結晶子径を実施例1と同様
に計算して求めた結果470Åであった。また、前記の
酸化セリウムの酸素吸蔵能の評価法に従って試験を行っ
た結果、OSCCは400℃で1.1mmol−O2/m
ol−CeO2、500℃で3.9mmol−O2/mo
l−CeO2であった。
Comparative Example 1 A cerium oxide powder was obtained in the same manner as in Example 1 except that the pH at the end of the reaction was 2.1. The crystallite size of this cerium oxide powder was calculated in the same manner as in Example 1 and found to be 470Å. In addition, as a result of performing a test according to the evaluation method of the oxygen storage capacity of cerium oxide, the OSCC was 1.1 mmol-O 2 / m at 400 ° C.
ol-CeO 2 , 3.9 mmol-O 2 / mo at 500 ° C.
It was 1-CeO 2 .

【0021】比較例2 実施例1において、セリウム塩としてCe(SO42
4H2Oを用い、最終pHを8.1とした以外は実施例1
と同様にして酸化セリウム粉末を得た。この酸化セリウ
ム粉末の結晶子径を実施例1と同様に計算して求めた結
果530Åであった。また、前記の酸化セリウムのCO
酸素吸蔵能の評価法に従って試験を行った結果、OSC
Cは400℃で1.0mmol−O2/mol−Ce
2、500℃で2.4mmol−O2/mol−CeO2
であった。
Comparative Example 2 In Example 1, as the cerium salt, Ce (SO 4 ) 2
Example 1 except that 4H 2 O was used and the final pH was 8.1.
Cerium oxide powder was obtained in the same manner as in. The crystallite size of this cerium oxide powder was calculated in the same manner as in Example 1 and the result was 530Å. In addition, CO of cerium oxide described above
As a result of performing a test according to the evaluation method of oxygen storage capacity, OSC
C is 1.0 mmol-O 2 / mol-Ce at 400 ° C.
O 2 , 2.4 mmol-O 2 / mol-CeO 2 at 500 ° C.
Met.

【0022】比較例3 実施例1において、セリウム塩として三価のCe2(S
43・8H2Oを用いた以外は実施例1と同様にして
酸化セリウム粉末を得た。この酸化セリウム粉末の結晶
子径を実施例1と同様に計算して求めた結果500Åで
あった。また、前記の酸化セリウムの酸素吸蔵能の評価
法に従って試験を行った結果、OSCCは400℃で
1.0mmol−O2/mol−CeO2、500℃で
2.7mmol−O2/mol−CeO2であった。
Comparative Example 3 In Example 1, trivalent Ce 2 (S) was used as the cerium salt.
O 4) except for using 3 · 8H 2 O was obtained cerium oxide powder in the same manner as in Example 1. The crystallite size of this cerium oxide powder was calculated in the same manner as in Example 1 and was found to be 500Å. Further, as a result of the test according to the evaluation method of the oxygen storage capacity of the cerium oxide, OSCC is 2.7mmol-O 2 / mol-CeO in 1.0mmol-O 2 / mol-CeO 2, 500 ℃ at 400 ° C. Was 2 .

【0023】比較例4 硫酸第二セリウム4水和物を300℃で加熱分解し、更
に900℃で3時間焼成して酸化セリウムを得た。この
酸化セリウム粉末の結晶子径は、上記のX線回折図の結
果からの計算で700Åであった。前記の酸化セリウム
の酸素吸蔵能の評価法に従って試験を行った結果、OS
CCは400℃で0.4mmol−O2/mol−CeO
2、500℃で1.6mmol−O2/mol−CeO2
あった。
Comparative Example 4 Cerium sulfate tetrahydrate was decomposed by heating at 300 ° C. and further calcined at 900 ° C. for 3 hours to obtain cerium oxide. The crystallite size of this cerium oxide powder was 700Å as calculated from the results of the above X-ray diffraction pattern. As a result of performing a test according to the above-mentioned evaluation method of oxygen storage capacity of cerium oxide,
CC is 0.4mmol-O 2 / mol-CeO at 400 ℃
2 was 1.6 mmol-O 2 / mol-CeO 2 at 500 ° C.

【0024】[0024]

【発明の効果】本発明によれば、最終的に得られた酸化
セリウムの結晶子径が小さく、従来よりも酸素吸蔵能の
大きく、担体へ分散性よく担持できる触媒を得ることの
できる水酸化セリウムおよび酸化セリウムの製造方法を
提供することができる。
INDUSTRIAL APPLICABILITY According to the present invention, hydroxylation can be obtained in which the finally obtained cerium oxide has a smaller crystallite size, a larger oxygen storage capacity than before, and can be supported on the carrier with good dispersibility. A method for producing cerium and cerium oxide can be provided.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 硫酸第二セリウム水溶液にアルカリを加
えて加水分解により水酸化セリウムを沈澱させる際、硫
酸第二セリウム水溶液にアルカリ水溶液を滴下し一旦生
成した水酸化セリウムが硫酸第二セリウム水溶液に再溶
解するまでアルカリ水溶液の滴下を一時中止し、完全に
再溶解させた後再びアルカリ水溶液の添加をする操作を
行い、生成した水酸化セリウムが再溶解しない状態の反
応液のpHが2.0以下で水酸化セリウムを析出せしめ
る反応を終了することを特徴とする水酸化セリウムの製
造方法。
1. When cerium hydroxide is precipitated by hydrolysis by adding an alkali to an aqueous solution of cerium sulfate, the aqueous alkali solution is dropped into the aqueous solution of cerium sulfate, and the cerium hydroxide once generated becomes an aqueous solution of cerium sulfate. The operation of adding the alkaline aqueous solution again after suspending the dropwise addition of the alkaline aqueous solution until it is redissolved and completely re-dissolving it, the pH of the reaction solution in a state in which the generated cerium hydroxide is not redissolved is 2.0. A method for producing cerium hydroxide, which comprises terminating the reaction for precipitating cerium hydroxide below.
【請求項2】 硫酸第二セリウム水溶液にアルカリを加
えて加水分解により水酸化セリウムを沈澱させる際、硫
酸第二セリウム水溶液にアルカリ水溶液を滴下し一旦生
成した水酸化セリウムが硫酸第二セリウム水溶液に再溶
解するまでアルカリ水溶液の滴下を一時中止し、完全に
再溶解させた後再びアルカリ水溶液の添加をする操作を
行い、生成した水酸化セリウムが再溶解しない状態の反
応液のpHが2.0以下で水酸化セリウムを析出せしめ
る反応を終了し、析出した水酸化セリウムを洗浄、乾
燥、焼成する酸化セリウムの製造方法。
2. When precipitating cerium hydroxide by hydrolysis by adding an alkali to an aqueous solution of cerium sulfate, the aqueous alkali solution is dropped into the aqueous solution of cerium sulfate, and the cerium hydroxide once produced becomes an aqueous solution of cerium sulfate. The operation of adding the alkaline aqueous solution again after suspending the dropwise addition of the alkaline aqueous solution until it is redissolved and completely re-dissolving it, the pH of the reaction solution in a state in which the generated cerium hydroxide is not redissolved is 2.0. A method for producing cerium oxide, in which the reaction for precipitating cerium hydroxide is terminated below, and the precipitated cerium hydroxide is washed, dried and calcined.
JP4037261A 1992-01-28 1992-01-28 Production of cerium hydroxide and cerium oxide Pending JPH05208816A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4037261A JPH05208816A (en) 1992-01-28 1992-01-28 Production of cerium hydroxide and cerium oxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4037261A JPH05208816A (en) 1992-01-28 1992-01-28 Production of cerium hydroxide and cerium oxide

Publications (1)

Publication Number Publication Date
JPH05208816A true JPH05208816A (en) 1993-08-20

Family

ID=12492721

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4037261A Pending JPH05208816A (en) 1992-01-28 1992-01-28 Production of cerium hydroxide and cerium oxide

Country Status (1)

Country Link
JP (1) JPH05208816A (en)

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US9242869B2 (en) 1997-09-19 2016-01-26 Opko Ireland Global Holdings, Ltd. Metal compounds mixed or sulphated, as phosphate binders
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US7473408B2 (en) 2002-04-15 2009-01-06 Lg Chem, Ltd. Method for preparing single crystalline cerium oxide powders
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US8418447B2 (en) 2004-09-09 2013-04-16 Toyota Jidosha Kabushiki Kaisha Exhaust gas cleaning catalyst, exhaust gas cleaning device, and system comprising internal combustion engine
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