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JPH0435223B2 - - Google Patents
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JPH0435223B2 - - Google Patents

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Publication number
JPH0435223B2
JPH0435223B2 JP58114341A JP11434183A JPH0435223B2 JP H0435223 B2 JPH0435223 B2 JP H0435223B2 JP 58114341 A JP58114341 A JP 58114341A JP 11434183 A JP11434183 A JP 11434183A JP H0435223 B2 JPH0435223 B2 JP H0435223B2
Authority
JP
Japan
Prior art keywords
manganese
catalyst
copper
precipitate
present
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 - Lifetime
Application number
JP58114341A
Other languages
Japanese (ja)
Other versions
JPS607940A (en
Inventor
Michiaki Yamamoto
Takashi Oogami
Noryuki Shimazaki
Yukio Kosakai
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.)
Mitsui Kinzoku Co Ltd
Original Assignee
Mitsui Mining and Smelting 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 Mitsui Mining and Smelting Co Ltd filed Critical Mitsui Mining and Smelting Co Ltd
Priority to JP58114341A priority Critical patent/JPS607940A/en
Publication of JPS607940A publication Critical patent/JPS607940A/en
Publication of JPH0435223B2 publication Critical patent/JPH0435223B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Oxygen, Ozone, And Oxides In General (AREA)
  • Catalysts (AREA)

Description

【発明の詳細な説明】 本発明はマンガンと銅とを含みガス中に含まれ
るオゾン(O3)を分解するオゾン分解用触媒の
製造方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing an ozone decomposition catalyst containing manganese and copper and decomposing ozone (O 3 ) contained in gas.

マンガンを含有する酸化触媒としては、マンガ
ン、銅、コバルト、銀などの可溶性塩を共沈させ
て得るホプカライト触媒が知られている。ホプカ
ライト触媒は低温における酸化触媒として、例え
ば防毒マスク用のCO除去剤に使用されている。
これまで各種のホプカライト触媒の改良触媒が提
案されているが、基本的にはいずれもホプカライ
ト触媒の性能を大巾に変えうるものではなく、低
温での触媒活性をさらに改善する必要があつた。
As an oxidation catalyst containing manganese, a hopcalite catalyst obtained by coprecipitating soluble salts of manganese, copper, cobalt, silver, etc. is known. Hopcalite catalysts are used as oxidation catalysts at low temperatures, such as CO removal agents for gas masks.
Various improved catalysts for hopcalite catalysts have been proposed so far, but basically none of them can significantly change the performance of hopcalite catalysts, and there is a need to further improve the catalytic activity at low temperatures.

しかし、最近新規な二酸化マンガン酸化触媒の
製法、例えば特開昭56−17637が提案されている。
この方法はアルカリ条件下で有機物を酸化するの
に使用した過マンガン酸カリから生成した副生二
酸化マンガン(アルカリ金属デルタ二酸化マンガ
ン)の懸濁液をつくり、銅、クロム、鉄、コバル
ト、ニツケル等の重金属の水酸化物が沈澱するよ
りも少くとも0.5低いPHでアルカリ金属と置換さ
せて重金属二酸化マンガン酸化触媒を製造する方
法である。この特定領域のPHで重金属とアルカリ
金属を置換させて触媒を製造している点が、アル
カリ金属デルタ二酸化マンガンより二酸化マンガ
ン酸化触媒をつくることを提案している米国特許
第3700605号より新規な方法となつている。
However, recently, new methods for producing manganese dioxide oxidation catalysts have been proposed, such as Japanese Patent Application Laid-Open No. 17637/1983.
This method creates a suspension of by-product manganese dioxide (alkali metal delta manganese dioxide) produced from potassium permanganate used to oxidize organic substances under alkaline conditions, and produces a suspension of copper, chromium, iron, cobalt, nickel, etc. This is a method for producing a heavy metal manganese dioxide oxidation catalyst by replacing the alkali metal with an alkali metal at a pH that is at least 0.5 lower than that at which the heavy metal hydroxide precipitates. The fact that the catalyst is produced by replacing heavy metals with alkali metals in this specific pH range is a new method compared to U.S. Patent No. 3,700,605, which proposes producing a manganese dioxide oxidation catalyst from alkali metal delta manganese dioxide. It is becoming.

一方、二酸化マンガンの表面に重金属を析出さ
せる方法としては無電解メツキ法が知られてい
る。この方法は二酸化マンガンを塩化第一錫を含
有するセンシタイザー液中に浸漬したのち別、
水洗し、次に塩化パラジウムを含有するアクチベ
ーター液中に浸漬して別、水洗する。その後、
重要な重金属無電解メツキ液で処理すれば二酸化
マンガン粒子の表面は重金属で被覆することがで
きる。この方法では無電解メツキの操作が煩雑で
処理費が高価につくといつた欠点を有している。
On the other hand, an electroless plating method is known as a method for depositing heavy metals on the surface of manganese dioxide. In this method, manganese dioxide is immersed in a sensitizer solution containing stannous chloride, and then separated.
It is washed with water, then immersed in an activator solution containing palladium chloride, and washed separately with water. after that,
The surface of manganese dioxide particles can be coated with heavy metals by treatment with an important heavy metal electroless plating solution. This method has drawbacks such as complicated electroless plating operations and high processing costs.

本発明者らはマンガンと銅を含有する酸化触媒
(ここでマンガンというのはマンガンおよびその
化合物を総称し、銅についても同様に化合物を含
む)について種々検討した結果、マンガンと銅を
含有する共沈澱物をつくる際にマンガン化合物の
一部を銅で同時に置換させる方法を見出した。こ
の方法はアルカリ金属デルタ二酸マンガンに特定
のPH領域で重金属を置換させるといつた触媒製造
方法と異なり製造工程が簡単で得られた触媒は低
温での酸化触媒活性が高いことを知見した。
The present inventors have conducted various studies on oxidation catalysts containing manganese and copper (here, manganese is a general term for manganese and its compounds, and similarly includes compounds for copper). We have discovered a method in which a part of the manganese compound is replaced with copper at the same time when forming a precipitate. It was found that this method has a simple manufacturing process and the resulting catalyst has high oxidation catalytic activity at low temperatures, unlike the catalyst manufacturing method in which heavy metals are substituted with alkali metal delta manganese dioate in a specific pH range.

また、かかる触媒を用いて低温でのO3の分解
性能を調べた結果、極めて優れたO3分解性能を
有することを知見した。
Furthermore, as a result of investigating the O 3 decomposition performance at low temperatures using such a catalyst, it was found that the catalyst had extremely excellent O 3 decomposition performance.

したがつて本発明の目的は、低温で優れたO3
分解性能を有するマンガンと銅を含有するオゾン
分解触媒を提供することにある。
Therefore, the object of the present invention is to provide excellent O 3 at low temperatures.
The object of the present invention is to provide an ozone decomposition catalyst containing manganese and copper that has decomposition performance.

本発明に係るオゾン分解用触媒の製造方法は、
マンガンおよび銅の可溶性塩の混合溶液に過酸化
水素水と過マンガン酸塩を含むアルカリ溶液とを
添加し、次いで沈澱物をろ別、脱水し、バインダ
を添加してねつ和した後、成形、乾燥することを
特徴とする。すなわち、本発明方法は基本的には
マンガンの可溶性塩と銅の可溶性塩の混合溶液中
に過酸化水素を添加したのち過マンガン酸塩を含
むアルカリ溶液で中和することまたは混合溶液を
前記アルカリ溶液で中和した後過酸化水素を添加
することによつて達成される。
The method for producing an ozone decomposition catalyst according to the present invention includes:
Aqueous hydrogen peroxide and an alkaline solution containing permanganate are added to a mixed solution of soluble salts of manganese and copper, then the precipitate is filtered and dehydrated, a binder is added and the mixture is wetted, and then molded. , characterized by drying. That is, the method of the present invention basically involves adding hydrogen peroxide to a mixed solution of a soluble manganese salt and a soluble copper salt, and then neutralizing it with an alkaline solution containing permanganate, or adding the mixed solution to the alkali solution. This is accomplished by adding hydrogen peroxide after neutralization with a solution.

本発明方法によつて得られたオゾン分解触媒は
X線回折分析によれば非晶質であり生成物を同定
することはできないが、本触媒は非晶質であるこ
とによつて特徴づけられる。また、示差熱分析に
よれば約500℃まで結晶水等の放出により重量が
漸減するマンガンと銅との化合物であることは判
つているが、化合物の化学式等については不明で
ある。
Although the ozone decomposition catalyst obtained by the method of the present invention is amorphous according to X-ray diffraction analysis and the product cannot be identified, the present catalyst is characterized by being amorphous. . Furthermore, although differential thermal analysis shows that it is a compound of manganese and copper whose weight gradually decreases by releasing crystal water etc. up to about 500°C, the chemical formula of the compound is unknown.

本発明方法により製造されたオゾン分解用触媒
は、例えば後記実施例の試験法による火災避難用
保護具等に関する基準に基ずいて実施した防煙試
験においてCO濃度を2500±250ppmにして30/
minの流速で触媒を通過させ触媒通過後のCO濃
度を測定したところ100ppm以下になり、350ppm
以下を合格基準と定めた上記基準を大巾に上廻る
性能であることが判つた。さらにまた後記実施例
の試験法によるO3分解試験において、O3濃度を
1〜5ppm含有する空気を10000〜150000HY-1の空
間速度で処理しても90%以上のO3分解性能を有
し、また500時間の耐久試験においてもO3分解性
能が劣化しないことが判つた。
The ozone decomposition catalyst produced by the method of the present invention was tested at a CO concentration of 2500±250ppm and 30%
When the CO concentration after passing through the catalyst was measured by passing through the catalyst at a flow rate of min, it was less than 100 ppm and 350 ppm.
It was found that the performance far exceeded the above-mentioned criteria, which set the following as acceptance criteria. Furthermore, in an O 3 decomposition test using the test method described in the Examples below, even when air containing an O 3 concentration of 1 to 5 ppm was treated at a space velocity of 10,000 to 150,000 HY-1 , it had an O 3 decomposition performance of 90% or more. However, it was also found that the O 3 decomposition performance did not deteriorate even in a 500-hour durability test.

以下に本発明触媒の製造方法の好ましい一例に
ついて詳しく説明する。
A preferred example of the method for producing the catalyst of the present invention will be described in detail below.

硝酸マンガン、硫酸マンガン、塩化マンガン等
のマンガンの可溶性塩を1当り0.05〜5モル、
好ましくは0.1〜0.3モル含む水溶液と硝酸銅、硫
酸銅、塩化銅等の銅の可溶性塩を1当り0.01〜
5モル、好しくは0.1〜0.3モル含む水溶液とを混
合する。この混合液1に対して酸化剤として過
酸化水素水0.01〜0.5モル、好しくは0.1〜0.2モル
を徐々に加える。過酸化水素水を添加して行くと
気泡がわずかに発生する。
0.05 to 5 mol of manganese soluble salts such as manganese nitrate, manganese sulfate, and manganese chloride,
Preferably, an aqueous solution containing 0.1 to 0.3 mol and a soluble salt of copper such as copper nitrate, copper sulfate, copper chloride, etc. per 0.01 to 0.3 mol per mol.
and an aqueous solution containing 5 mol, preferably 0.1 to 0.3 mol. 0.01 to 0.5 mol, preferably 0.1 to 0.2 mol of hydrogen peroxide is gradually added to this mixed solution 1 as an oxidizing agent. As the hydrogen peroxide solution is added, a small amount of air bubbles will be generated.

この時点に達したら過マンガン酸塩のアルカリ
金属塩を1当り0.01〜0.15モル、好しくは0.05
〜0.1モル含む水溶液にしたのち、水酸化カリウ
ムまたは水酸化ナトリウムを1当り1〜10モ
ル、好しくは5〜10モル含む水溶液中に混合した
アルカリ溶液を上記過酸化水素水を添加した混合
溶液中に徐々に添加していくと黒褐色の沈澱物が
生成し急激に気泡が発生する。気泡の発生してい
る間に添加を終了させる方が沈澱物の酸化には良
い。上記アルカリ溶液は加温して添加してもよい
しまたは室温で添加してもよい。得られた沈澱物
を十分に撹拌したのち静置して上澄液をデカンテ
ーシヨンにより除去し、加温した脱イオン水でリ
パルプとデカンテーシヨンを2〜3度繰返す。上
澄液のPHが9.5以下、好ましくは9以下になつた
のち遠心分離機により別する。この状態に達す
ると本発明によるマンガンと銅を含有する生成物
が得られるので、それを100℃前後の温度で生乾
き状態まで脱水し、もし必要ならば活性炭ゼオラ
イト、ベントナイト、活性アルミナ等の吸着剤を
添加し、アルミナゾル、ケイ酸ソーダ等のバイン
ダーを沈澱物100部に対してその乾量基準で3〜
30重量部、好しくは5〜15重量部添加して十分に
ねつ和したのちペレツターで必要な形状に成形
し、100〜150℃で数時間乾燥すると本発明による
触媒が得られる。
Once this point is reached, add 0.01 to 0.15 mol per alkali metal salt of permanganate, preferably 0.05
After making an aqueous solution containing ~0.1 mol, an alkaline solution mixed in an aqueous solution containing 1 to 10 mol of potassium hydroxide or sodium hydroxide, preferably 5 to 10 mol per unit, and the above hydrogen peroxide solution is added to the mixed solution. When it is gradually added to the liquid, a blackish brown precipitate is formed and bubbles suddenly appear. It is better for oxidation of the precipitate to end the addition while bubbles are being generated. The alkaline solution may be added while being heated or at room temperature. The obtained precipitate is sufficiently stirred and left to stand, and the supernatant liquid is removed by decantation, and the repulping and decantation are repeated two to three times with heated deionized water. After the pH of the supernatant becomes 9.5 or less, preferably 9 or less, it is separated using a centrifuge. Once this state is reached, a product containing manganese and copper according to the invention is obtained, which is dehydrated to a semi-dry state at temperatures around 100°C and, if necessary, adsorbents such as activated carbon zeolite, bentonite, activated alumina, etc. and binder such as alumina sol, sodium silicate, etc. on a dry weight basis per 100 parts of precipitate.
The catalyst according to the present invention is obtained by adding 30 parts by weight, preferably 5 to 15 parts by weight, thoroughly stirring the mixture, molding it into the required shape using a pelleter, and drying it at 100 to 150 DEG C. for several hours.

上記本発明触媒において、マンガンおよび銅以
外の他の重金属を排除する必要はない。例えば
鉄、コバルト、ニツケル、銀、希土類元素等が金
属のまま、またはそれらの化合物として混合溶液
中に存在してもよいしまたは活性炭、ゼオライト
等の吸着剤と混在してもよい。
In the above catalyst of the present invention, it is not necessary to exclude heavy metals other than manganese and copper. For example, iron, cobalt, nickel, silver, rare earth elements, etc. may be present in the mixed solution as metals or as compounds thereof, or may be mixed with adsorbents such as activated carbon and zeolite.

次に本発明を実施例で具体的に説明するが、本
発明はこれによつて限定されるものではない。
EXAMPLES Next, the present invention will be specifically explained using Examples, but the present invention is not limited thereto.

実施例 1 硫酸マンガン(MnSO4・OH2O)1900grをイ
オン交換水に溶して液量を50にする。硫酸銅
(CuSO4・5H2O)500grをイオン交換水に溶して
液量を13にする。ついでこれらの溶液を室温で
全量混合し、撹拌しながら過酸化水素水(30%)
1を添加する。
Example 1 Dissolve 1900gr of manganese sulfate ( MnSO4.OH2O ) in ion-exchanged water to make the liquid volume 50g. Dissolve 500g of copper sulfate (CuSO 4 5H 2 O) in ion-exchanged water to make the liquid volume 13. Next, mix all of these solutions at room temperature, and add hydrogen peroxide (30%) while stirring.
Add 1.

過マンガン酸カリウム(KMnO4)170grをイ
オン交換水に溶して液量を1.1にした溶液を苛
性ソーダ1050grをイオン交換水に溶して液量を
3.5にした溶液中に混合したアルカリ溶液を添
加していく。沈澱物が生成したのち約1時間撹拌
して静置する。沈澱物が沈降後、上澄液を分離し
温イオン交換水を加えて沈澱物をリパルプし同様
な操作を行う。上澄液のPHが9.5以下になれば遠
心分離機で別する。
Dissolve 170g of potassium permanganate (KMnO 4 ) in ion-exchanged water to make the liquid volume 1.1. Dissolve 1050g of caustic soda in ion-exchanged water and reduce the liquid volume.
Add the mixed alkaline solution to the solution adjusted to 3.5. After a precipitate is formed, the mixture is stirred and left to stand for about 1 hour. After the precipitate has settled, the supernatant liquid is separated, warm ion-exchanged water is added to repulp the precipitate, and the same operation is performed. If the pH of the supernatant drops to below 9.5, separate it using a centrifuge.

得られたケーキを100〜110℃で約4時間乾燥し
て生乾きの状態にし、アルミナゾル(10%)
500grを加えてニーダーでねつ和後ペレツターで
直径1.5mmのペレツトに成形し150℃で5時間乾燥
して製品とした。
The resulting cake was dried at 100 to 110°C for about 4 hours to a half-dry state, and then treated with alumina sol (10%).
500 gr was added and the mixture was kneaded using a kneader, formed into pellets with a diameter of 1.5 mm using a pelleter, and dried at 150°C for 5 hours to obtain a product.

得られた製品を分析した結果、Mn:57%、
Cu:12%を含有し非晶質であつた。
As a result of analyzing the obtained product, Mn: 57%,
It contained Cu: 12% and was amorphous.

実施例 2 実施例1と同様にして得た沈澱物を生乾きの状
態にし、乾量基準で1000grに対して活性炭200gr
とアムミナゾル(10%)600grを加えて実施例1
と同様にしてマンガン触媒を得た。
Example 2 The precipitate obtained in the same manner as in Example 1 was brought to a half-dried state, and 200 gr of activated carbon was added to 1000 gr on a dry basis.
Example 1 by adding 600gr of amminazole (10%)
A manganese catalyst was obtained in the same manner as above.

比較例 1、2 実施例1、2において、過酸化水素を用いない
こと以外は同様に操作したものをそれぞれ比較例
1、2とした。
Comparative Examples 1 and 2 Comparative Examples 1 and 2 were obtained by performing the same operations as in Examples 1 and 2, except that hydrogen peroxide was not used.

試験例 O3分解試験は次の条件で行つた。Test Example O 3 The decomposition test was conducted under the following conditions.

O3発生機より得られたO3を混合した空気を水
に通して加湿し、直径20mmの円筒容器に充填した
実施例1および実施例2並びに比較例1、2で得
られたペレツト触媒10ml中を1〜30/minの流
速で流し、触媒層通過前後の混合空気中のO3
度を分析してO3分解性能を測定した。
Air mixed with O 3 obtained from an O 3 generator was passed through water and humidified, and 10 ml of pellet catalysts obtained in Examples 1 and 2 and Comparative Examples 1 and 2 were filled into a cylindrical container with a diameter of 20 mm. The O 3 decomposition performance was measured by flowing through the mixture at a flow rate of 1 to 30/min and analyzing the O 3 concentration in the mixed air before and after passing through the catalyst layer.

試験結果は第1図および第2図に示した。 The test results are shown in FIGS. 1 and 2.

上記試験結果から明らかなように本発明のマン
ガン触媒は低温における一酸化炭素の除去効果お
よびオゾンの分解効果が格段に優れていることが
判る。
As is clear from the above test results, the manganese catalyst of the present invention is extremely effective in removing carbon monoxide and decomposing ozone at low temperatures.

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

第1図および第2図は空間速度ないし試験時間
に対するオゾンの分解効率を示すグラフである。
Figures 1 and 2 are graphs showing ozone decomposition efficiency versus space velocity or test time.

Claims (1)

【特許請求の範囲】[Claims] 1 マンガンおよび銅の可溶性塩の混合溶液に過
酸化水素水と過マンガン酸塩を含むアルカリ溶液
とを添加し、次いで沈澱物をろ別、脱水し、バイ
ンダを添加してねつ和した後、成形、乾燥するこ
とを特徴とするオゾン分解用触媒の製造方法。
1. Add hydrogen peroxide solution and an alkaline solution containing permanganate to a mixed solution of soluble salts of manganese and copper, then filter the precipitate, dehydrate it, add a binder to make it wet, A method for producing an ozone decomposition catalyst, which comprises molding and drying.
JP58114341A 1983-06-27 1983-06-27 Manganese catalyst Granted JPS607940A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58114341A JPS607940A (en) 1983-06-27 1983-06-27 Manganese catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58114341A JPS607940A (en) 1983-06-27 1983-06-27 Manganese catalyst

Publications (2)

Publication Number Publication Date
JPS607940A JPS607940A (en) 1985-01-16
JPH0435223B2 true JPH0435223B2 (en) 1992-06-10

Family

ID=14635343

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58114341A Granted JPS607940A (en) 1983-06-27 1983-06-27 Manganese catalyst

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JP2010069444A (en) * 2008-09-19 2010-04-02 Takeshi Sonoda Catalyst for decomposing ozone and method for manufacturing the same

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JPH02273512A (en) * 1989-04-15 1990-11-08 Shin Nippon Koa Kk Filter for removal of ozone
CN102580759A (en) * 2011-01-18 2012-07-18 中国科学院生态环境研究中心 Water purification method capable of realizing in-situ preparation and in-situ regeneration of catalyst and catalyzing zone to oxidize organic micropollutants

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010069444A (en) * 2008-09-19 2010-04-02 Takeshi Sonoda Catalyst for decomposing ozone and method for manufacturing the same

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