JPH11179378A - Method for decomposing oxygen-containing organic compounds having one carbon atom contained in wastewater - Google Patents
Method for decomposing oxygen-containing organic compounds having one carbon atom contained in wastewaterInfo
- Publication number
- JPH11179378A JPH11179378A JP9365868A JP36586897A JPH11179378A JP H11179378 A JPH11179378 A JP H11179378A JP 9365868 A JP9365868 A JP 9365868A JP 36586897 A JP36586897 A JP 36586897A JP H11179378 A JPH11179378 A JP H11179378A
- Authority
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- Japan
- Prior art keywords
- oxygen
- containing organic
- organic compound
- catalyst
- wastewater
- 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.)
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- Catalysts (AREA)
- Removal Of Specific Substances (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
(57)【要約】
【課題】 炭素数が1つの含酸素有機化合物を湿式酸化
法により分解する方法において、酸化剤を用いることな
く、100℃以下の温度及び常圧下でその含酸素有機化
合物を分解する方法を提供する。
【解決手段】 炭素数が1つの含酸素有機化合物を含む
排水を酸素含有ガスと共に貴金属担持活性炭触媒層を装
填した反応槽100℃以下の温度で通過させて、該含酸
素有機化合物を酸化分解させることを特徴とする排水中
に含まれる前記含酸素有機化合物の分解方法。(57) Abstract: In a method for decomposing an oxygen-containing organic compound having one carbon atom by a wet oxidation method, the oxygen-containing organic compound is decomposed at a temperature of 100 ° C. or less and at normal pressure without using an oxidizing agent. A method for disassembly is provided. SOLUTION: A wastewater containing an oxygen-containing organic compound having one carbon atom is passed with a oxygen-containing gas at a temperature of 100 ° C. or lower in a reaction vessel equipped with a noble metal-supported activated carbon catalyst layer to oxidatively decompose the oxygen-containing organic compound. A method for decomposing the above oxygen-containing organic compound contained in wastewater.
Description
【0001】[0001]
【発明の属する技術分野】本発明は種々のプロセスから
排出されるメタノール、ホルムアルデヒド、蟻酸及び蟻
酸塩等の炭素数が1つの含酸素有機化合物を含む排水を
100℃以下において酸素の存在下触媒と接触させて分
解除去する方法に関する。BACKGROUND OF THE INVENTION The present invention relates to a method for treating wastewater containing oxygen-containing organic compounds having one carbon atom such as methanol, formaldehyde, formic acid and formate discharged from various processes at a temperature of 100 ° C. or less and a catalyst in the presence of oxygen. The present invention relates to a method of decomposing and removing by contact.
【0002】[0002]
【従来の技術】メタノール、ホルムアルデヒド、蟻酸
(或いはその塩)の如き炭素数が1つの含酸素有機化合
物は、他のより分子量の大きい有機化合物と共存してい
る場合が多く、COD処理或いはBOD処理という形で
一括して生物処理されているケースが多い。こうした生
物処理は常温、常圧で行えるため安定性に富み運転管理
が容易な点に特徴がある。しかしながら常温の生物反応
であるため、反応速度が遅く、槽容積が大きくなり、場
所をとることと、生物処理につきものの発生汚泥処理が
必要となる欠点を有している。こうした生物処理の欠点
を回避するべく、湿式酸化法が提案されている。この方
法は、触媒或いは酸化剤を用いることにより、有機化合
物の酸化反応を促進し、汚泥の発生のない、よりコンパ
クトな装置を実現するものである。しかしながら、特公
昭59−19757号、特開昭49−44556号等で
提案されている方法は、100℃以上、実際には200
℃以上の温度で、数10kg/cm2の圧力下で運転す
るものであり、装置規模は小さくなるが、運転管理がた
いへん面倒となる。また、オゾンや過酸化水素等の非塩
素系酸化剤を添加すれば、100℃以下の常圧条件下
で、含酸素有機物の酸化分解を可能とすることができる
が、酸化剤のコストがそのまま排水の処理費を押し上げ
てしまうことになり好ましくない。2. Description of the Related Art Oxygen-containing organic compounds having one carbon atom, such as methanol, formaldehyde and formic acid (or a salt thereof), often coexist with other organic compounds having a higher molecular weight, and are subjected to COD treatment or BOD treatment. In many cases, biological treatment is performed collectively in the form of Since such biological treatment can be performed at normal temperature and normal pressure, it is characterized by high stability and easy operation management. However, since it is a biological reaction at room temperature, the reaction rate is slow, the tank volume is large, the space is large, and there are drawbacks in that sludge treatment, which is required for biological treatment, is required. In order to avoid such disadvantages of biological treatment, a wet oxidation method has been proposed. This method promotes the oxidation reaction of an organic compound by using a catalyst or an oxidizing agent, and realizes a more compact apparatus without generation of sludge. However, the methods proposed in JP-B-59-19775, JP-A-49-44556, and the like, require a temperature of 100 ° C. or more,
The device is operated at a temperature of not less than ° C. and under a pressure of several tens of kg / cm 2 , and although the device scale is small, operation management is very troublesome. Further, if a non-chlorine oxidizing agent such as ozone or hydrogen peroxide is added, oxidative decomposition of oxygen-containing organic substances can be performed under normal pressure conditions of 100 ° C. or less, but the cost of the oxidizing agent remains unchanged. This is undesirable because it increases the cost of treating wastewater.
【0003】[0003]
【発明が解決しようとする課題】本発明は、炭素数が1
つの含酸素有機化合物を湿式酸化法により分解する方法
において、酸化剤を用いることなく、100℃以下の温
度及び常圧下でその含酸素有機化合物を分解する方法を
提供することをその課題とする。DISCLOSURE OF THE INVENTION The present invention relates to a method for producing a compound having 1 carbon atom.
An object of the present invention is to provide a method for decomposing two oxygen-containing organic compounds by a wet oxidation method without using an oxidizing agent and decomposing the oxygen-containing organic compound at a temperature of 100 ° C. or lower and at a normal pressure.
【0004】[0004]
【発明が解決するための手段】本発明者らは、前記課題
を解決すべく鋭意研究を重ねた結果、本発明を完成する
に至った。即ち本発明によれば、炭素数が1つの含酸素
有機化合物を含む排水を酸素含有ガスと共に貴金属担持
活性炭触媒層を装填した反応槽100℃以下の温度で通
過させて、該含酸素有機化合物を酸化分解させることを
特徴とする排水中に含まれる前記含酸素有機化合物の分
解方法が提供される。Means for Solving the Problems The present inventors have made intensive studies to solve the above-mentioned problems, and as a result, completed the present invention. That is, according to the present invention, a wastewater containing an oxygen-containing organic compound having one carbon atom is passed at a temperature of 100 ° C. or lower together with an oxygen-containing gas at a temperature of 100 ° C. or less in a reaction vessel equipped with a noble metal-supported activated carbon catalyst layer. A method for decomposing the oxygen-containing organic compound contained in wastewater, which is characterized by oxidative decomposition.
【0005】[0005]
【発明の実施と形態】本発明は、炭素数が1つの含酸素
有機化合物(以下、単に被処理化合物とも言う)の酸化
分解用触媒として、活性炭に担持された貴金属触媒を用
いる。この場合、貴金属触媒を担持させるための活性炭
の種類については特に限定する必要はなく、一般市販品
で良い。一例を挙げれば、活性炭の原料は、やしがら、
石炭、木炭、ピートなどいずれでも良い。また、物性は
表面積が500m2/g以上、細孔容積が0.4cc/
g以上あるものが好ましいが、ほとんどの市販品の活性
炭は、この要件を満たしているので問題はない。BEST MODE FOR CARRYING OUT THE INVENTION In the present invention, a noble metal catalyst supported on activated carbon is used as a catalyst for oxidative decomposition of an oxygen-containing organic compound having one carbon atom (hereinafter simply referred to as a compound to be treated). In this case, the type of activated carbon for supporting the noble metal catalyst does not need to be particularly limited, and may be a general commercial product. To give an example, the raw material of activated carbon is palm,
Any of coal, charcoal, peat, etc. may be used. The physical properties are as follows: the surface area is 500 m 2 / g or more, and the pore volume is 0.4 cc / g.
g is preferred, but most commercial activated carbons satisfy this requirement and do not pose a problem.
【0006】この活性炭に担持する酸化活性を有する金
属としては、貴金属を用いる。この、貴金属としては、
特にPt、Pd、Rh、Ru、Os、Irが好ましい。
V、Mn、Cu等に代表される卑金属は前者に比べ低温
活性に劣るために本発明には適さない。貴金属の担持量
は少な過ぎると低温酸化が困難となるのである値以上担
持する必要がある。その値は金属の種類によらず0.0
1wt%以上であり、好ましくは0.1wt%以上であ
る。その上限値は1wt%程度である。それより多い金
属の担持は多くの場合効果がなく不要である。触媒の担
持方法は貴金属が数10Åのクラスターとして良好に分
散されるような方法が必要である。しかし、これは、各
貴金属の水溶性錯化合物を必要量水に溶解させた後、活
性炭を含浸させ、これを乾燥させ、不活性ガス中で加熱
分解させることにより容易に実現できるものである。A noble metal is used as the oxidizing metal supported on the activated carbon. As this noble metal,
Particularly, Pt, Pd, Rh, Ru, Os, and Ir are preferable.
Base metals typified by V, Mn, Cu and the like are inferior in low-temperature activity as compared with the former, and therefore are not suitable for the present invention. If the amount of the noble metal carried is too small, low-temperature oxidation becomes difficult. The value is 0.0 regardless of the type of metal.
It is at least 1 wt%, preferably at least 0.1 wt%. The upper limit is about 1 wt%. Supporting more metal is often ineffective and unnecessary. A method for supporting the catalyst requires a method in which the noble metal is well dispersed as clusters of several tens of degrees. However, this can be easily realized by dissolving a required amount of the water-soluble complex compound of each noble metal in water, impregnating with activated carbon, drying this, and thermally decomposing it in an inert gas.
【0007】本発明は、その触媒に活性炭に担持した貴
金属を用いるとともに、低温酸化を可能とするために、
流通形式の反応装置を用いる。常圧下では、水中への酸
素の溶存量は極めて小さいので、触媒は活性点近傍まで
ガス状酸素が到達する流通形式の反応装置を用いる必要
がある。本発明者らは、触媒の粒子サイズとその形状、
そして液とガスの流通形式がこの気液接触効率に大きく
影響することを見出した。触媒サイズを大きくし過ぎる
ことは触媒有効係数を低下せしめるので好ましくないこ
とは周知の事実である。その点触媒粒子サイズを小さく
することは活性を大きくするので一般に好ましいといわ
れている。しかし、本発明の場合、触媒の粒子サイズを
小さくしていくと、ガスと液の流れが不均一となりかえ
って活性が低下することが見出された。触媒の粒子径を
小さくしていくと活性が上昇するのは、触媒の代表径が
1mm迄であり、それを超すと活性はむしろ低下するこ
とが分かった。この場合触媒の代表径(d)とは、触媒
粒子1個の外表面積をS、体積をVとすると下式で表現
されるものである。 この触媒の形状は出来るだけガスと液が均一に流れるよ
うなもので、特に液だまりの出来ないようなものが好ま
しい。その点に於ては、球状及び円柱状が好ましい。単
なる破砕片、鞍状もの、板状もの、表面に凸凹があるも
の、二重円筒構造のものなどは厚い液膜あるいは液だま
りが出来易く、低温活性を発揮しにくくなるので避ける
べきである。[0007] The present invention uses a noble metal supported on activated carbon for the catalyst and enables low-temperature oxidation.
A flow-type reactor is used. Under normal pressure, the dissolved amount of oxygen in water is extremely small, so it is necessary to use a flow-type reactor in which gaseous oxygen reaches the vicinity of the active point as the catalyst. The present inventors have determined the particle size and shape of the catalyst,
It has been found that the flow form of the liquid and the gas greatly affects the gas-liquid contact efficiency. It is a well-known fact that too large a catalyst size is not preferable because it reduces the catalyst effectiveness factor. In this regard, it is generally said that reducing the catalyst particle size is preferable because it increases the activity. However, in the case of the present invention, it has been found that as the particle size of the catalyst is reduced, the flow of gas and liquid becomes uneven, and the activity is reduced. It was found that the activity increases when the particle size of the catalyst is reduced as the representative diameter of the catalyst is up to 1 mm. In this case, the representative diameter (d) of the catalyst is expressed by the following equation, where S is the outer surface area of one catalyst particle and V is the volume. The shape of the catalyst is such that the gas and liquid flow as uniformly as possible, and in particular, it is preferable that the catalyst and liquid are not formed. In that respect, spherical and cylindrical shapes are preferred. Simple fragments, saddles, plates, bumps on the surface, double cylinders, etc. should be avoided because they tend to form a thick liquid film or pool and make it difficult to exhibit low-temperature activity.
【0008】次に、本発明者らは、この触媒層に排水及
び酸素含有ガスを流す形式について検討し、液を上向き
に流す方式では酸素の吸収速度が非常に小さくなるの
で、液は下向きに流すべきであることを見出した。これ
は上向流では触媒全体が水に浸り、ガスはその中を気泡
状態で通過するため酸素が透過するべき液膜が厚く且つ
ガス液接触界面の面積も小さくなるためであろうと考え
られる。また、ガス速度が触媒表面の液膜の厚みを左右
することは良く知られた事実であるが、本発明の場合、
そのガスの線速は、空塔速度で1.0cm/sec以上
に保持するのが好ましい。その上限値は、通常100c
m/sec程度である。Next, the present inventors studied a method of flowing drainage water and an oxygen-containing gas through the catalyst layer. In the method of flowing the liquid upward, the rate of oxygen absorption is extremely small, and the liquid is directed downward. I found that it should be washed away. This is considered to be because in the upward flow, the entire catalyst is immersed in water, and the gas passes through it in a bubble state, so that the liquid film through which oxygen should pass is thick and the area of the gas-liquid contact interface is small. It is well known that the gas velocity affects the thickness of the liquid film on the catalyst surface, but in the case of the present invention,
The linear velocity of the gas is preferably maintained at 1.0 cm / sec or more at the superficial velocity. The upper limit is usually 100c
m / sec.
【0009】本発明の被処理対象となる含酸素有機化合
物には、メタノール、ホルムアルデヒド、蟻酸及び蟻酸
塩が包含されるが、本発明の上限温度である100℃に
近い温度で反応させる場合には、エタノール、ハロメタ
ン類、エチレングリコール等の酸化分解も可能である。The oxygen-containing organic compound to be treated in the present invention includes methanol, formaldehyde, formic acid and formate, but when the reaction is carried out at a temperature close to the upper limit temperature of 100 ° C. of the present invention. Oxidative degradation of ethanol, halomethanes, ethylene glycol and the like is also possible.
【0010】[0010]
【実施例】次に本発明を実施例によりさらに詳細に説明
する。 実施例1 市販の0.2wt%Pt担持球状活性炭触媒(直径約
1.5mm)1リットルを断熱型流通式反応装置に充填
した。次にこの反応器内に上方より1mol/lの濃度
の蟻酸ナトリウム水溶液を予め60℃に温め、1リット
ル/hrで流し、同時に上方より空気を300Nl/h
rの速度で流通せしめた。この時蟻酸の燃焼熱による水
温の上昇は水の蒸発潜熱でキャンセルされ、反応器出口
の液温は66℃であった。流出液を冷却した後TOC濃
度計で有機炭素濃度を測定して蟻酸Naの分解率を求め
たところ、98.8%であった。Next, the present invention will be described in more detail with reference to examples. Example 1 One liter of a commercially available 0.2 wt% Pt-supported spherical activated carbon catalyst (about 1.5 mm in diameter) was charged into an adiabatic flow reactor. Next, an aqueous solution of sodium formate having a concentration of 1 mol / l was preliminarily heated to 60 ° C. and flowed at a rate of 1 liter / hr from above into the reactor.
It was distributed at a rate of r. At this time, the rise in water temperature due to the heat of combustion of formic acid was canceled by the latent heat of evaporation of water, and the liquid temperature at the outlet of the reactor was 66 ° C. After cooling the effluent, the organic carbon concentration was measured by a TOC densitometer to determine the decomposition rate of Na formate, which was 98.8%.
【0011】実施例2 市販の0.5wt%Pd担持活性炭の柱状物(直径約1
mm、平均長さ約2mm)を実施例1に記載の反応器に
1リットル充填した。次にこの反応器内に上方より0.
5mol/lのメタノール水溶液を常温(25℃)で1
リットル/hrの速度で流し、同時に空気を200Nl
/hrの速度で流下せしめた。この時の反応器出口の液
温は30℃であった。流出液を密閉フラスコ中で冷却さ
せた後、TOC濃度計で有機炭素濃度を測定し、メタノ
ールの転化率を求めたところ、94%であった。Example 2 A column of commercially available 0.5 wt% Pd-supported activated carbon (having a diameter of about 1
mm, average length about 2 mm) was charged to the reactor described in Example 1 as 1 liter. Next, from the top in this reactor, 0.1.
A 5 mol / l aqueous methanol solution was added at room temperature (25 ° C.)
Flow at a rate of 1 liter / hr and at the same time 200 Nl of air
/ Hr. At this time, the liquid temperature at the outlet of the reactor was 30 ° C. After the effluent was cooled in a closed flask, the organic carbon concentration was measured with a TOC densitometer, and the conversion of methanol was determined to be 94%.
【0012】実施例3 直径1.6mmφの活性炭に0.2wt%のPdと0.
3wt%のRuを担持した触媒を実施例1に記載の反応
器に1リットル充填した。次に、この反応器内に上方よ
り0.5mol/lのホルマリン水溶液を40℃に予熱
して0.5リットル/hrの速度で流し、同時に空気を
200Nl/hrの速度で流下せしめた。この時の反応
器出口液温は44℃であった。流出液を密閉フラスコに
とり、この中で常温迄冷却させた後、TOC濃度計で有
機炭素濃度を測定してホルマリンの分解率を求めたとこ
ろ、97.5%であった。Example 3 0.2% by weight of Pd and 0.1% in activated carbon having a diameter of 1.6 mm.
One liter of the catalyst supporting 3 wt% of Ru was charged into the reactor described in Example 1. Next, a 0.5 mol / l formalin aqueous solution was preheated to 40 ° C. from above and flowed at a rate of 0.5 liter / hr from above, and air was simultaneously allowed to flow down at a rate of 200 Nl / hr. The reactor outlet liquid temperature at this time was 44 ° C. The effluent was placed in a sealed flask, cooled to room temperature, and the organic carbon concentration was measured with a TOC densitometer to determine the formalin decomposition rate, which was 97.5%.
【0013】[0013]
【発明の効果】本発明によれば、排水中に含まれる炭素
数が1つの含酸素有機化合物を、常圧において、100
℃以下の湿式条件下で効率よく酸化分解することができ
る。According to the present invention, the oxygen-containing organic compound having one carbon atom contained in the waste water is converted to 100 at normal pressure.
It can be efficiently oxidatively decomposed under a wet condition of not more than ℃.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI C02F 1/72 ZAB C02F 1/72 ZABZ (72)発明者 西島 裕明 神奈川県横浜市鶴見区鶴見中央二丁目12番 1号 千代田化工建設株式会社内 (72)発明者 広浜 誠也 神奈川県横浜市鶴見区鶴見中央二丁目12番 1号 千代田化工建設株式会社内────────────────────────────────────────────────── ─── Continued on the front page (51) Int.Cl. 6 Identification code FI C02F 1/72 ZAB C02F 1/72 ZABZ (72) Inventor Hiroaki Nishijima 2-1-1, Tsurumichuo, Tsurumi-ku, Yokohama-shi, Kanagawa Chiyoda (72) Inventor Seiya Hirohama 2-1-1 Tsurumi Chuo, Tsurumi-ku, Yokohama-shi, Kanagawa Prefecture Inside Chiyoda Chemical Works, Ltd.
Claims (4)
排水を酸素含有ガスと共に貴金属担持活性炭触媒層を装
填した反応槽に100℃以下の温度で通過させて、該含
酸素有機化合物を酸化分解させることを特徴とする排水
中に含まれる前記含酸素有機化合物の分解方法。1. A wastewater containing an oxygen-containing organic compound having one carbon atom is passed at a temperature of 100 ° C. or lower together with an oxygen-containing gas through a reaction tank equipped with a noble metal-supported activated carbon catalyst layer to oxidize the oxygen-containing organic compound. A method for decomposing the oxygen-containing organic compound contained in wastewater, characterized by decomposing the oxygen-containing organic compound.
テニウム、ロジウム、オスミウム、イリジウムの中から
選ばれる少なくとも1種を活性炭に0.01wt%以上
担持した触媒である請求項1に記載の方法。2. The method according to claim 1, wherein the noble metal-supported catalyst is a catalyst in which at least one selected from platinum, palladium, ruthenium, rhodium, osmium, and iridium is supported on activated carbon in an amount of 0.01 wt% or more.
の代表径が1mm以上である請求項2に記載の方法。3. The method according to claim 2, wherein the shape of the catalyst is spherical or cylindrical, and its representative diameter is 1 mm or more.
に向って排水を流下させる請求項1〜3のいずれかに記
載の方法。4. The method according to any one of claims 1 to 3, wherein the wastewater is caused to flow downward from above in the catalyst layer in the reaction tank.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9365868A JPH11179378A (en) | 1997-12-22 | 1997-12-22 | Method for decomposing oxygen-containing organic compounds having one carbon atom contained in wastewater |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9365868A JPH11179378A (en) | 1997-12-22 | 1997-12-22 | Method for decomposing oxygen-containing organic compounds having one carbon atom contained in wastewater |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH11179378A true JPH11179378A (en) | 1999-07-06 |
Family
ID=18485321
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9365868A Pending JPH11179378A (en) | 1997-12-22 | 1997-12-22 | Method for decomposing oxygen-containing organic compounds having one carbon atom contained in wastewater |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH11179378A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002253966A (en) * | 2000-12-28 | 2002-09-10 | Nippon Shokubai Co Ltd | Catalyst for waste water treatment and manufacturing method thereof and method of treating waste water |
| WO2003076348A1 (en) * | 2002-03-11 | 2003-09-18 | Nippon Shokubai Co., Ltd. | Method for treating waste water |
| JP2003334571A (en) * | 2002-03-11 | 2003-11-25 | Nippon Shokubai Co Ltd | Method for treating drain |
-
1997
- 1997-12-22 JP JP9365868A patent/JPH11179378A/en active Pending
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002253966A (en) * | 2000-12-28 | 2002-09-10 | Nippon Shokubai Co Ltd | Catalyst for waste water treatment and manufacturing method thereof and method of treating waste water |
| WO2003076348A1 (en) * | 2002-03-11 | 2003-09-18 | Nippon Shokubai Co., Ltd. | Method for treating waste water |
| JP2003334571A (en) * | 2002-03-11 | 2003-11-25 | Nippon Shokubai Co Ltd | Method for treating drain |
| CN1323036C (en) * | 2002-03-11 | 2007-06-27 | 株式会社日本触媒 | Waste water treatment method |
| US7247240B2 (en) | 2002-03-11 | 2007-07-24 | Nippon Shokubai Co., Ltd. | Method for treating waste water |
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