JPS607940A - Manganese catalyst - Google Patents
Manganese catalystInfo
- Publication number
- JPS607940A JPS607940A JP58114341A JP11434183A JPS607940A JP S607940 A JPS607940 A JP S607940A JP 58114341 A JP58114341 A JP 58114341A JP 11434183 A JP11434183 A JP 11434183A JP S607940 A JPS607940 A JP S607940A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- manganese
- copper
- soluble
- permanganate
- 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.)
- Granted
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
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Oxygen, Ozone, And Oxides In General (AREA)
- Catalysts (AREA)
Abstract
Description
【発明の詳細な説明】
本発明はマンガンと銅を含み力゛スqコに含くまれる一
酸化炭素(CO)全1余去する触〃哄およびノfス中に
含く寸れるオゾン(0,)を分力子するf独〃裟に関す
る。DETAILED DESCRIPTION OF THE INVENTION The present invention removes all of the carbon monoxide (CO) contained in gas containing manganese and copper, as well as the ozone (contained in NOF). 0,) is related to f unique.
マンカンを含有する酸化触媒としては、マンカン、銅、
コバルト、銀などの可溶性塩全共沈させて得るホブカラ
イド触媒が知られている。Oxidation catalysts containing mankan include mankan, copper,
A fobcalide catalyst obtained by co-precipitating all soluble salts such as cobalt and silver is known.
ボブカライド触媒は低温における酸イし触媒として、例
えば防毒マスク用のCO除去斉1]にイ吏用されている
。これまで各種のホフ゛カライド1g虫媒の改良触媒が
提案されてはいるが、基本的にはいずれもホブカライド
触媒の性能全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った。Bobcalide catalysts are used as acidification catalysts at low temperatures, for example, for CO removal for gas masks. Up to now, various improved catalysts using 1 g of phocalide as insect carriers have been proposed, but basically none of them can change the overall performance of the phocalide catalyst, and it is necessary to further improve the catalytic activity at low temperatures. there were.
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
法はアルカリ両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(αデルク二酸化マンガン)の懸濁液をつくり、
銅、クロム、鉄、コバルト、ニッケル等の重金属の水酸
化物が沈澱するよりも少くとも05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fY−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イしマンガンより二階fヒマンガン
酸化触媒をつくることを提案している米国特許第3,7
00,605号より新規な方法となっている。However, recently a new method for producing a manganese dioxide oxidation catalyst has been proposed, for example, Japanese Patent Application Laid-Open No. 17637/1983. This method creates a suspension of by-product manganese dioxide (alkali gold (alpha manganese dioxide)) produced from potassium permanganate used to oxidize organic matter under alkaline conditions.
This is a method for producing a heavy metal manganese dioxide oxidation catalyst by substituting an alkali metal at a pH that is at least 0.5 liters lower than the pH at which the hydroxides of heavy metals such as copper, chromium, iron, cobalt, and nickel precipitate. The fact that a catalyst is produced by substituting a heavy metal with an alkali metal fY at a pH in this specific range is reflected in U.S. Patent No. ,7
No. 00,605 is a new method.
一方、二酸化マンガンの表面に重金4を析出させる方法
としては無電解メ0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−
液中に浸漬したのち戸別、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戸別、水洗す
る。On the other hand, an electroless plating method is known as a method for depositing heavy metal 4 on the surface of manganese dioxide. This method combines manganese dioxide with a sensitizer containing stannous chloride.
After being immersed in a liquid, the pieces are washed door-to-door with water, and then immersed in an activator solution containing palladium chloride and washed door-to-door with water.
その後、必要な重金属無電解メッ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ッキの操作が煩雑で処理費が高
価につくといった欠点4有している。Thereafter, the surface of the manganese dioxide particles can be coated with a heavy metal by treating with a necessary heavy metal electroless plating solution. This method has disadvantages 4 in that the electroless plating operation is complicated and the processing cost is high.
本発明辞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合む)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的物を゛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ニ酸マンカ
ンに特定のP H領域で重金属を置換させるといった触
媒製造方法と異なり製造工程が簡Φ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 inventors of the present invention have conducted various studies on oxidation catalysts containing manganese and copper (here, manganese refers to manganese and its compounds collectively, and also includes copper compounds). We have discovered a method in which a part of the manganese compound is replaced with copper at the same time when producing a coprecipitate. It was found that this method differs from the catalyst manufacturing method in which heavy metals are substituted with alkali metal delta mankanate in a specific PH range, and that the catalyst obtained by the simple manufacturing process has high oxidation catalytic activity at low temperatures.
したがって本発明の目的は、低温で酸化活性の高いマン
ガンと銅を含有する酸化触媒を提供することにある。同
時に本発明による触媒を用いて低温でのO5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。Therefore, an object of the present invention is to provide an oxidation catalyst containing manganese and copper that has high oxidation activity at low temperatures. At the same time, as a result of examining the O5 decomposition performance at low temperatures using the catalyst according to the present invention, it was found that the catalyst had extremely excellent O3 decomposition performance.
したがって本発明の他の目的は、低温で優れた08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。本発明によるマンガンと銅を含有
する触媒は基本的にはマンガンの可溶性塩と銅の可溶性
塩の混合溶液中に酸化剤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酸化剤全添加することによ
って達成される。得られた生成物はX線回折分析によれ
ば非晶質であり生成物全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って特徴ずけられる。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
判っているが、化′合物の化学式等については不明であ
る。Therefore, another object of the present invention is to provide an ozone decomposition catalyst containing manganese and copper that has excellent O8 decomposition performance at low temperatures. The catalyst containing manganese and copper according to the present invention is basically produced by adding an oxidizing agent to a mixed solution of a soluble salt of manganese and a soluble salt of copper, and then neutralizing or mixing with an alkaline solution containing permanganate. This is achieved by neutralizing the solution with the alkaline solution and then adding the entire oxidizing agent. The resulting product is amorphous according to X-ray diffraction analysis, and the product cannot be completely identified, but the present catalyst is characterized by its amorphous nature. Also, according to differential thermal analysis, it is known that it is a compound of manganese and copper whose weight gradually decreases by releasing water of crystallization up to about 500°C, but the chemical formula of the compound is unknown.
本発明触媒は、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すいて実施した防煙試験
においてCO濃度全2500±250ppmにして30
”mi n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1100pp以下になり、350
p pm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フh0さらにまた後記実施例
の試j倹法によるOs分解試;険において、03濃度を
1〜5 ppm含有する空気を10,000〜150,
000HY−1の空間速度で処理しても90チ以上の0
3分解性能を有し、また500時間の耐久試験に2いて
もO3分解性能が劣化しないことが判った。The catalyst of the present invention was found to have a total CO concentration of 2,500 ± 250 ppm in a smoke prevention test conducted based on the standards for fire evacuation protective equipment, etc. according to the test method described in Examples below.
The CO after passing through the catalyst is
When the concentration was measured, it was less than 1100pp, which was 350pp.
It was found that the performance far exceeded the above-mentioned standard, which set the acceptance standard as below p pm. 10,000 to 150 ppm of air,
Even if processed at a spatial velocity of 000HY-1, 0 of more than 90 inches
It was found that the O3 decomposition performance did not deteriorate even after a 500 hour durability test.
1メ下に本発明触媒の製造方法の好ましい一例11ζつ
いて詳しく説明する。One preferred example of the method for producing the catalyst of the present invention, 11ζ, will be explained in detail below.
硝酸マンガン、硫酸マンガン、塩化−Zンガン等のマン
ガンの可溶性塩を1を当り005〜5モル、好しくけ0
.1〜0.3モル含む水溶液と硝酸銅。Soluble salts of manganese such as manganese nitrate, manganese sulfate, Zn chloride, etc. per 1 mol, preferably 0
.. An aqueous solution containing 1 to 0.3 mol of copper nitrate.
硫酸銅、塩化銅等の銅の可溶性塩を1を当り001〜5
モル、好しくけ0.1〜0.3モル含む水溶液とを混合
する。この混合?ff1ltに対して酸化剤として過酸
化水素水0.01〜0.5モル、好しくけ0.1〜0、
2モルを徐々に加える。過酸化水素水全添加して行くと
気泡がわずかに発生する。Copper soluble salts such as copper sulfate and copper chloride per 001 to 5
mol, preferably an aqueous solution containing 0.1 to 0.3 mol. This mixture? 0.01 to 0.5 mol of hydrogen peroxide as an oxidizing agent, preferably 0.1 to 0, per ff1lt;
Gradually add 2 moles. When all the hydrogen peroxide solution is added, a slight amount of 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を当りO8旧〜0.15モル、好しくけ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
水酸化ナトリゲム′f:1を当り1〜10モル、好しく
け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
を十分に攪拌したのち静置して上澄液をデカンテーショ
ンにより除去し、加温した脱イオン水でリパルプとデカ
ンテーションを2〜3度繰返す。上澄液のPl(が9.
5以下、好ましくは9以下になったのち遠心分離機によ
り戸別する。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too’
c@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。Once this point is reached, add the alkali metal salt of permanganate to 0.15 mole of O8 per 1 part, preferably 0.05 to 0.
.. After making an aqueous solution containing 1 mol of potassium hydroxide or sodium hydroxide 'f:1, the above hydrogen peroxide solution was added to an alkaline solution mixed in an aqueous solution containing 1 to 10 mol, preferably 5 to 10 mol, of potassium hydroxide or sodium hydroxide 'f:1. When it is gradually added to the mixed solution, a blackish brown precipitate is formed and bubbles are suddenly generated. 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 then left to stand, the supernatant liquid is removed by decantation, and the repulping and decantation are repeated two to three times with heated deionized water. Pl of the supernatant (9.
After it becomes 5 or less, preferably 9 or less, it is separated from house to house using a centrifuge. Once this state is reached, a manganese and copper containing product according to the invention is obtained, which can be
Dehydrate to half-dry state at the temperature after c@, and use activated carbon zeolite if necessary.
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′へ叫部、好しくけ
5〜15重量部添加して十分にねつ和したのち一ペレツ
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。Adsorbents such as bentonite and activated alumina are added, and binders such as alumina sol and sodium silicate are added to the precipitate.
Add 5 to 15 parts by weight, preferably 5 to 15 parts by weight, based on the dry weight of 3 to 30 parts per part, and thoroughly homogenize, form into the required shape using a pelletizer, and heat at 100 to 150°C. After drying for several hours, a catalyst according to the invention is obtained.
):配本発明触媒に2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、
ニッケル、銀、希土類元素等が金1川のまま、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。): It is not necessary to exclude heavy metals other than manganese and copper in the catalyst of the present invention. For example, iron, cobalt,
Nickel, silver, rare earth elements, etc. may be present in the mixed solution as gold or as a compound thereof, or may be mixed with an adsorbent such as activated carbon or 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
nによって限定されるものではない。EXAMPLES Next, the present invention will be specifically explained with reference to Examples, but the present invention is not limited thereto.
実施例−1
硫酸マンガフ (MnSO,・OH,0)1,900g
rをイオン交換水に溶して液量′f、50tにする。硫
酸銅(α幻4・5H,0) 500 gr fイオン交
換水に溶して液量を13tにする。ついでこれらの溶液
を室温で全量混合し、攪拌しながら過酸化水素水(30
%ン1tを添加する。Example-1 Manga sulfate (MnSO, .OH, 0) 1,900g
Dissolve r in ion-exchanged water to make a liquid volume 'f of 50 t. Copper sulfate (α phantom 4, 5H, 0) 500 gr fDissolve in ion-exchanged water to make a liquid volume of 13 tons. Next, these solutions were mixed in their entirety at room temperature, and hydrogen peroxide solution (30%
Add 1 t of %.
過マンガン酸カリウム(f(MnO4) 170 g
rをイオン交換水に溶して液酸を1゜1tにした溶液を
苛性ソーダ10105Oをイオン交換水に溶して液量を
3.5t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時間攪拌して静置す
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Th IJバルブし同様な操作を行う。上
澄液のPHが95以下になれば遠心分離機で戸別する。Potassium permanganate (f(MnO4) 170 g
An alkaline solution mixed with a solution prepared by dissolving r in ion-exchanged water to make a liquid acid of 1°1 t and a solution prepared by dissolving caustic soda 10105O in ion-exchanged water to make a liquid amount of 3.5 t is added. 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, the precipitate Th IJ valve is used, and the same operation is performed. When the pH of the supernatant drops below 95, it is separated using a centrifuge.
得られたクーキを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
ヲ加えてニーグーでねつ和後ペレツターで直径1.5財
のペレットに成形し1−50℃で5時間乾燥して製品と
した。The obtained cookie was dried at 100 to 110°C for about 4 hours to a half-dry state, and 500g of alumina sol (10%) was added.
After addition, the mixture was kneaded using a Nigu machine, formed into pellets with a diameter of 1.5 pieces using a pelletizer, and dried at 1-50°C for 5 hours to obtain a product.
得られた製品全分析した結果、Mn : 57%、Cu
:12%を含有し非晶質であった。As a result of complete analysis of the obtained product, Mn: 57%, Cu
:12% and was amorphous.
実施例−2
実施例−1と同様にして得た沈澱物全生乾きの状1.財
にし、乾量基準で1,000grに対して活性炭200
grとアルミナゾル(io%) 600grをカロえて
実施例−1と同様にしてマンガン触媒を得た。Example-2 Precipitate obtained in the same manner as in Example-1, completely dried 1. Activated carbon 200g per 1,000g on dry basis
A manganese catalyst was obtained in the same manner as in Example 1 except that 600 gr of gr and alumina sol (io%) were added.
試験例−1 触媒性能試験は次の条件で行った。Test example-1 The catalyst performance test was conducted under the following conditions.
火災避))IE用保護具等の試験方法及び判断基準に基
ず@集煙箱に、木材のくん焼煙及び−酸化炭素濃度れ、
入力側煙濃度計内の煙及びガス濃度をそれぞれ0.7±
0.1(減光係数) 、 2500±250 ppm
K ari 74倹する。Fire prevention)) Based on the test methods and criteria for IE protective equipment, etc., the smoke collection box contains wood smoke and -carbon oxide concentration.
The smoke and gas concentrations in the input side smoke density meter are each 0.7±.
0.1 (attenuation coefficient), 2500±250 ppm
K ari 74 save money.
この煙を30t/−の通気量で供試防煙マスクを通し、
煙濃度、−酸化炭素濃度および通気抵抗値を測定する。This smoke was passed through a test smoke mask with an airflow rate of 30t/-.
Measure the smoke concentration, carbon oxide concentration and ventilation resistance value.
この試験において、煙濃度Q、l/m以下、−酸化炭素
濃度350ppm以下で、かつ、通気抵抗値50mAq
以下となる時間が3分以上を合格とする。In this test, the smoke concentration Q was 1/m or less, the carbon oxide concentration was 350 ppm or less, and the ventilation resistance was 50 mAq.
If the time is below 3 minutes or more, it is considered a pass.
触媒性能の測定方法は直径約80m5の円筒管に100
tの触媒を充填し、その上に等敞のゼオライトと活性炭
の混合物を充填し、上記試験ガスがゼオライト側から入
って触媒を通過するようにする。この時のガスの入口側
と出口側の濃度および通気抵抗値を測定した。The method for measuring catalyst performance is to place 100
A mixture of zeolite and activated carbon of equal strength is charged on top of the catalyst, so that the test gas enters from the zeolite side and passes through the catalyst. At this time, the gas concentration and ventilation resistance on the inlet and outlet sides of the gas were measured.
試験結果は表−1に示した。比較触媒として市販ホブカ
ライドについてもその結果を併記し表−1
試験例−2
03分解試1倹は次の条件で行った。The test results are shown in Table-1. The results of commercially available fobucalide as a comparative catalyst are also listed in Table 1. Test Example 2 03 Decomposition Test 1 was carried out under the following conditions.
03発生機より得られた03を混合した空気を水に通し
て加湿し、直径2ONRの円筒容器に充填した実施例−
1分よび実施例−2で得られたベレット触媒10mt中
を1〜3017mの流速で流し、触媒層通過前後の混合
空気中の0.濃度を分析して03分解性能全測定した。Example in which air mixed with 03 obtained from a 03 generator was humidified by passing it through water and filled into a cylindrical container with a diameter of 2 ONR.
1 minute and flowed through 10 mt of the pellet catalyst obtained in Example-2 at a flow rate of 1 to 3017 m, and 0.0 m in the mixed air before and after passing through the catalyst layer. The concentration was analyzed and the 03 decomposition performance was completely measured.
試験結果は図−1および図−2に糸した。The test results are shown in Figures 1 and 2.
上記状)倹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 results, the manganese catalyst of the present invention is extremely effective in removing carbon monoxide and decomposing ozone at low temperatures.
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。
特許出願 人 三井金属鉱業株式会社
代理人 弁理士 光石士部(他1名)Figures 1 and 2 are graphs showing ozone decomposition efficiency versus space velocity or test time. Patent applicant Mitsui Mining & Mining Co., Ltd. agent Patent attorney Shibu Mitsuishi (1 other person)
Claims (1)
マンガン酸塩を含むアルカ1ノ溶液を添加することを特
徴とするマンガ′ンおよび銅ならびにそれらの化合物か
らなるマンガン融媒。A manganese melting medium consisting of manganese and copper and their compounds, characterized in that an alkali solution containing an oxidizing agent and a permanganate is added to a solution of soluble salts of manganese and copper.
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 true JPS607940A (en) | 1985-01-16 |
| JPH0435223B2 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 |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS607940A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| 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 |
Families Citing this family (1)
| 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 |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5120477A (en) * | 1974-08-12 | 1976-02-18 | Toyo Enterprise Ltd | Senshakiniokeru taiyatsuyadashihohooyobi dosochi |
-
1983
- 1983-06-27 JP JP58114341A patent/JPS607940A/en active Granted
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5120477A (en) * | 1974-08-12 | 1976-02-18 | Toyo Enterprise Ltd | Senshakiniokeru taiyatsuyadashihohooyobi dosochi |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| 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 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0435223B2 (en) | 1992-06-10 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JPS6233540A (en) | Divalent metal-aluminate catalyst | |
| JP4364798B2 (en) | Method for producing manganese compound and method for using the same | |
| CN101132856A (en) | Aggregate of precipitated silica, method for the production thereof and use thereof as filter medium in gas filtration | |
| JPH06509984A (en) | Catalytic cracking method of silver-containing carrier catalyst and dinitrogen monoxide | |
| JP5568726B2 (en) | Titanium oxide / layered double hydroxide composite and method for producing the same | |
| CN107555481A (en) | A kind of Mn oxide material and preparation method thereof | |
| US1809978A (en) | Process of producing hydrogen | |
| JP2002355558A (en) | Method for removing formaldehyde by oxidation | |
| JPS6068034A (en) | Process for removing poisonous component | |
| JPS607940A (en) | Manganese catalyst | |
| JP3578259B2 (en) | Decomposition and removal of formaldehyde in air | |
| JP3457953B2 (en) | Nitrogen oxide and / or sulfur oxide adsorbent | |
| US4112053A (en) | Dry method for the denitrification of exhaust gas containing nitrogen oxides | |
| JP3339204B2 (en) | Nitrogen oxide oxidation adsorbent and nitrogen oxide removal method | |
| JPH02144125A (en) | Method for purifying exhaust gas | |
| JPH0217220B2 (en) | ||
| CN113019423B (en) | Catalyst for oxidizing ammonia gas by ozone, preparation method and application thereof | |
| JP2994065B2 (en) | Method for producing metal composite oxide powder | |
| JP2002320847A (en) | Adsorbent for nitrogen oxide and/or sulfur oxide and method for removing nitrogen oxide and/or sulfur oxide | |
| JPS6038972B2 (en) | Ozone decomposition catalyst | |
| JPS6137980B2 (en) | ||
| CN100488605C (en) | Catalysts for removing H2S from gas streams, methods for their preparation and uses thereof | |
| JP3362918B2 (en) | Exhaust gas purification method | |
| JP3634795B2 (en) | Nitrogen oxide and / or sulfur oxide adsorbent | |
| JP6119042B2 (en) | Air treatment equipment |