JP4066527B2 - Treatment of wastewater containing hydrogen peroxide and ammonia - Google Patents

Treatment of wastewater containing hydrogen peroxide and ammonia Download PDF

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Publication number
JP4066527B2
JP4066527B2 JP22309398A JP22309398A JP4066527B2 JP 4066527 B2 JP4066527 B2 JP 4066527B2 JP 22309398 A JP22309398 A JP 22309398A JP 22309398 A JP22309398 A JP 22309398A JP 4066527 B2 JP4066527 B2 JP 4066527B2
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Japan
Prior art keywords
ammonia
hydrogen peroxide
water
containing hydrogen
less
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JP22309398A
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Japanese (ja)
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JP2000051871A (en
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敏次 中原
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、半導体工場等から排出される過酸化水素とアンモニアとを含む排水を効率的に処理する方法に関する。
【0002】
【従来の技術】
半導体の製造プロセスからは、過酸化水素とアンモニアとを含む排水が排出される。この排水中の過酸化水素はCODMnにかかるため分解する必要がある。また、アンモニアは河川、湖沼、海の富栄養化の原因となるため処理する必要がある。
【0003】
従来、排水中のアンモニアのみを除去する方法としては、生物処理による方法があるが、生物処理による方法には、汚泥が発生する;維持管理が困難である;反応速度が遅く、広い装置設置面積を必要とする;などの短所がある。
【0004】
排水中の過酸化水素はカタラーゼ等の薬剤を加えることにより分解処理されているが、この方法では、薬剤の注入量の制御が難しく、安定した水質を得るのが困難であった。
【0005】
このような問題を解決し、排水中の過酸化水素とアンモニアを同時に効率的に分解除去する方法として、本出願人は、先に、貴金属担持触媒を用いて両成分を分解する方法を提案した(特開平5−269475号公報)。
【0006】
【発明が解決しようとする課題】
特開平5−269475号公報に開示される貴金属担持触媒による接触分解法では、高温、高圧での操作が必要であり、イニシャルコストが高いという問題があった。
【0007】
本発明はこのような問題を解決し、排水中の過酸化水素及びアンモニアを、比較的低温、低圧の操作条件で安全にかつ効率的に処理することができる過酸化水素とアンモニアとを含む排水の処理法を提供することを目的とする。
【0008】
【課題を解決するための手段】
本発明の過酸化水素とアンモニアとを含む排水の処理法は、過酸化水素とアンモニアとを含む排水を、20℃以上〜100℃未満かつ常圧以下〜液相が維持できる圧力の条件下で、触媒有効成分として、白金、パラジウム、ルテニウム、ロジウム、インジウム、イリジウム、銀、金、コバルト、銅、ニッケル及びタングステン、並びにこれらの金属の水不溶性又は水難溶性の化合物から選ばれる1種又は2種以上を担体に担持した触媒と接触させて該排水中の過酸化水素を分解し、過酸化水素の分解により発生する酸素ガスを系外へ排出した後、20℃以上〜100℃未満かつ常圧以下の条件下でアンモニアを揮散させて除去することを特徴とする。
【0009】
本発明の方法においては、排水中の過酸化水素のみを接触分解(2H22→2H2O+O2)するため、高温、高圧の操作条件を必要とすることなく、温度100℃未満、圧力常圧以下というような比較的低温、低圧の操作条件で接触分解を行える。
【0010】
過酸化水素を分解除去した後の排水中に残留するアンモニアは、揮散させることにより容易に除去することができる。揮散させたアンモニアは凝縮させて回収し、再利用しても良く、また、触媒空気酸化により分解処理しても良い。
【0011】
なお、排水中の過酸化水素のみを接触分解するために過酸化水素の接触分解に先立ってアンモニアを揮散させた場合には、同時に過酸化水素の分解による酸素ガスが発生し、熱効率の低下や、酸素ガスとアンモニアガスとの気爆性混合ガスが生じる等の短所がある。
【0012】
本発明によれば、過酸化水素を接触分解除去した後アンモニアを揮散除去することにより、安全かつ効率的な処理を行える。
【0013】
【発明の実施の形態】
以下に本発明を図面を参照して詳細に説明する。
【0014】
図1は本発明の過酸化水素とアンモニアとを含む排水の処理法の実施の形態を示す系統図である。
【0015】
過酸化水素(H22)及びアンモニア(NH3)を含有する排水(原水)は、まず、過酸化水素分解装置1に導入して過酸化水素の接触分解を行う。
【0016】
この接触分解装置1としては、触媒を充填した固定床式反応塔を用いるのが好ましい。
【0017】
本発明において、触媒としては、触媒有効成分として、白金、パラジウム、ルテニウム、ロジウム、インジウム、イリジウム、銀、金、コバルト、銅、ニッケル及びタングステン、並びにこれらの金属の水不溶性又は水難溶性の化合物、具体的には、一酸化コバルト、過酸化コバルト、一酸化ニッケル、二酸化ルテニウム、三二酸化ロジウム、一酸化パラジウム、二酸化イリジウム、酸化第二銅、二酸化タングステン等の酸化物から選ばれる1種又は2種以上を、アルミナ、活性炭、酸化チタン、ジルコニア、ゼオライト、その他の合成樹脂等の担体に担持したものも挙げられる。担持触媒中の金属及び/又はその化合物の担持量は、通常、担体重量の0.05〜25重量%、好ましくは0.5〜10重量%であることが望ましい。このような担持触媒は、球状、ペレット状、円柱状、破砕片状、ハニカム状、粉末状等の種々の形態で使用可能であり、固定床式反応搭に使用する担持触媒の粒径は、通常0.2〜10mm、特に0.5〜5mm程度であることが好ましい。
【0018】
また、固定床式反応塔への通液条件は、排水の過酸化水素濃度や用いる触媒によっても異なるが、本発明では、アンモニアを分解させずに過酸化水素のみを分解するため、次のような比較的低温、低圧の条件を採用することができる。
【0019】
[通液条件]
温度: 100℃未満、好ましくは20〜90℃
圧力: 常圧以下(液相が維持できる圧力であれば良い。)
流速: SV1〜100hr-1、好ましくは10〜50hr-1
また、排水のpHが7未満の酸性であると過酸化水素の分解速度が小さくなるので、pH7以上、特にpH7〜13であることが好ましい。
【0020】
過酸化水素分解装置1では、原水中の過酸化水素が水と酸素に分解され、酸素ガスは系外へ排出される。
【0021】
過酸化水素分解装置1の処理水は、過酸化水素を殆ど含まず、アンモニアが残留するものであるが、本発明では、この水をアンモニア揮散搭2に導入して、水中のアンモニアを揮散させて除去する。
【0022】
このアンモニアの揮散除去法としては、ストリッピング法、蒸発法(蒸留法を含む)等公知のすべての方法を採用することができるが、その操作条件としては、100℃未満、常圧以下の低温、低圧条件を採用するのが好ましく、具体的には、次のような方法を採用することができる。
【0023】
(i) 水温20℃以上で、気液比(G/L)1000〜5000倍で空気、窒素ガス等によりストリッピングする。
(ii) 水温60℃以上にて、蒸気量/処理量比5〜20%で蒸気でストリッピングする。
(iii) 水温60℃以上にて、蒸気量/処理量比5〜60%、還流比1〜7で蒸留する。
【0024】
このようにしてアンモニアを揮散除去した処理水は、系外へ排出される。
【0025】
なお、揮散されたアンモニアガスは、必要に応じて凝縮させて回収し、ウエハ洗浄等に有効利用することができる。
【0026】
また、このアンモニアガスは、触媒空気酸化分解により分解除去しても良い。
【0027】
この触媒空気酸化分解に用いる触媒としては、上記過酸化水素の分解触媒と同様(但し活性炭を除く)のものを用いることができる。
【0028】
【実施例】
以下に実施例を挙げて、本発明をより具体的に説明する。
【0029】
実施例1
アンモニア性窒素:1250mg/L、過酸化水素:6000mg/L、pH10.5の合成排水を調製し、これを原水として、まず、過酸化コバルト担持ゼオライト触媒(コバルト担持量2.5重量%、平均粒径2mm)を60mL充填したカラムに、下記条件で通液した。
【0030】
[通液条件]
温度:20℃
圧力:常圧
流速:370mL/hr(SV=6hr-1
流出液中の過酸化水素濃度は2mg/L以下、アンモニア性窒素濃度は1200mg/Lであった。
【0031】
この流出液1000mLを、内径50mm、高さ1500mmのアクリル樹脂カラムに直径3mmのガラスビーズを充填した揮散搭に入れ、下部より散気管で空気を50NL/minの速度で吹き込み(G/L=3000倍)、1時間処理した(水温60℃)。処理後の水中に残留するアンモニア性窒素の濃度は、60mg/Lであった。
【0032】
一方、揮散処理において発生した揮散ガス中のアンモニアの平均濃度は600ppm(容量比)であった。
【0033】
この揮散ガスを330℃に加熱した後、酸化触媒搭(内径50mmのステンレス製反応塔に0.5重量%白金担持γ−アルミナ酸化触媒を150mL充填した反応塔)に空塔速度(SV)20000hr-1で通気した後、還元触媒搭(内径50mmのステンレス製反応塔にバナジウム−チタニア系還元触媒を500mL充填した反応塔)に空塔速度(SV)6000hr-1で通気した。
【0034】
得られた処理ガスのアンモニア濃度は1ppm(容量比)以下、NOX濃度は10ppm(容量比)以下であった。
【0035】
実施例2
アンモニア性窒素:2000mg/L、過酸化水素:6000mg/L、SiO2:2mg/L、pH11.0の合成排水を調製し、これを原水として、まず、0.5重量%白金担持チタニア触媒(平均粒径1.5mm)を60mL充填したカラムに、下記条件で通液した。
【0036】
[通液条件]
温度:60℃
圧力:常圧
流速:1200mL/hr(SV=30hr-1
流出液中の過酸化水素濃度は2mg/L以下、アンモニア性窒素濃度は1800mg/Lであった。
【0037】
この処理液1000mLを、2Lの枝付きフラスコを用いて100℃で単蒸留操作をして1.8倍に濃縮した。
【0038】
得られた凝縮水中のアンモニア性窒素濃度は3900mg/L、SiO2濃度は1mg/L以下であった。また、濃縮水中のアンモニア性窒素濃度は60mg/Lであった。
【0039】
【発明の効果】
以上詳述した通り、本発明の過酸化水素とアンモニアとを含む排水の処理法によれば、
▲1▼ 排水中の過酸化水素及びアンモニアを比較的低温、低圧の操作条件で安全にかつ効率的に処理することができる。
▲2▼ 生物処理に比べて維持管理が容易であり、また、装置設置面積を小さくすることができる上に汚泥の発生もない。
▲3▼ 薬剤の添加が不要である。
▲4▼ アンモニアを回収して有効利用することもできる。
等の効果が奏される。
【図面の簡単な説明】
【図1】本発明の過酸化水素とアンモニアとを含む排水の処理法の実施の形態を示す系統図である。
【符号の説明】
1 過酸化水素分解装置
2 アンモニア揮散搭
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for efficiently treating wastewater containing hydrogen peroxide and ammonia discharged from a semiconductor factory or the like.
[0002]
[Prior art]
Wastewater containing hydrogen peroxide and ammonia is discharged from the semiconductor manufacturing process. Since the hydrogen peroxide in the wastewater is applied to COD Mn , it must be decomposed. Ammonia also needs to be treated because it causes eutrophication of rivers, lakes, and seas.
[0003]
Conventionally, as a method of removing only ammonia in waste water, there is a method by biological treatment, but in the method by biological treatment, sludge is generated; maintenance is difficult; reaction rate is slow, and a large equipment installation area There are disadvantages such as;
[0004]
Hydrogen peroxide in the wastewater is decomposed by adding a chemical such as catalase. However, in this method, it is difficult to control the injection amount of the chemical and it is difficult to obtain a stable water quality.
[0005]
As a method of solving such problems and efficiently decomposing and removing hydrogen peroxide and ammonia in the wastewater simultaneously, the present applicant has previously proposed a method of decomposing both components using a noble metal-supported catalyst. (JP-A-5-269475).
[0006]
[Problems to be solved by the invention]
In the catalytic cracking method using a noble metal-supported catalyst disclosed in JP-A-5-269475, there is a problem that operation at high temperature and high pressure is required, and initial cost is high.
[0007]
The present invention solves such problems, and wastewater containing hydrogen peroxide and ammonia capable of safely and efficiently treating hydrogen peroxide and ammonia in waste water under relatively low temperature and low pressure operating conditions. It aims at providing the processing method of.
[0008]
[Means for Solving the Problems]
The method for treating wastewater containing hydrogen peroxide and ammonia according to the present invention comprises treating wastewater containing hydrogen peroxide and ammonia under conditions of a pressure at which the liquid phase can be maintained at 20 ° C. to less than 100 ° C. and below normal pressure. As an active ingredient of the catalyst, one or two selected from platinum, palladium, ruthenium, rhodium, indium, iridium, silver, gold, cobalt, copper, nickel and tungsten, and a water-insoluble or poorly water-soluble compound of these metals. more decomposing hydrogen peroxide of the exhaust water in contact with the catalyst supported on a carrier, after discharging the oxygen gas generated by the decomposition of hydrogen peroxide from the system, 20 ° C. or higher to 100 ° C. below and normal It is characterized by volatilizing and removing ammonia under the conditions below the pressure .
[0009]
In the method of the present invention, only hydrogen peroxide in the waste water is catalytically decomposed (2H 2 O 2 → 2H 2 O + O 2 ), so that the operating conditions of high temperature and high pressure are not required, the temperature is less than 100 ° C., the pressure Catalytic cracking can be performed under relatively low temperature and low pressure operating conditions such as normal pressure and below.
[0010]
Ammonia remaining in the waste water after decomposing and removing hydrogen peroxide can be easily removed by volatilization. Volatilized ammonia may be condensed, recovered, reused, or decomposed by catalytic air oxidation.
[0011]
In addition, when ammonia is volatilized prior to the catalytic decomposition of hydrogen peroxide to catalytically decompose only the hydrogen peroxide in the wastewater, oxygen gas is simultaneously generated due to the decomposition of hydrogen peroxide, resulting in a decrease in thermal efficiency. There are disadvantages such as the generation of an explosive gas mixture of oxygen gas and ammonia gas.
[0012]
According to the present invention, safe and efficient treatment can be performed by volatilizing and removing ammonia after catalytic decomposition and removal of hydrogen peroxide.
[0013]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the present invention will be described in detail with reference to the drawings.
[0014]
FIG. 1 is a system diagram showing an embodiment of a method for treating waste water containing hydrogen peroxide and ammonia according to the present invention.
[0015]
Waste water (raw water) containing hydrogen peroxide (H 2 O 2 ) and ammonia (NH 3 ) is first introduced into the hydrogen peroxide decomposition apparatus 1 to perform catalytic decomposition of hydrogen peroxide.
[0016]
As the catalytic cracking apparatus 1, it is preferable to use a fixed bed type reaction tower packed with a catalyst.
[0017]
In the present invention, as the catalyst, catalyst as medium an active ingredient, platinum, palladium, ruthenium, rhodium, indium, iridium, silver, gold, cobalt, copper, nickel and tungsten, as well as water-insoluble compounds or poorly soluble of these metals Specifically, one or two selected from oxides such as cobalt monoxide, cobalt peroxide, nickel monoxide, ruthenium dioxide, rhodium trioxide, palladium monoxide, iridium dioxide, cupric oxide, and tungsten dioxide. The thing which carry | supported seed | species or more on support | carriers, such as an alumina, activated carbon, a titanium oxide, a zirconia, a zeolite, and another synthetic resin, is also mentioned. The supported amount of the metal and / or the compound thereof in the supported catalyst is usually 0.05 to 25% by weight, preferably 0.5 to 10% by weight of the support weight. Such collateral lifting catalysts, spherical, pellet-like, cylindrical, spall shape, a honeycomb shape, may be used in various forms of powder, etc., grains responsible lifting catalysts to use in a fixed bed reactor tower The diameter is usually about 0.2 to 10 mm, particularly about 0.5 to 5 mm.
[0018]
In addition, although the conditions for passing through the fixed bed type reaction tower vary depending on the concentration of hydrogen peroxide in the waste water and the catalyst used, in the present invention, only hydrogen peroxide is decomposed without decomposing ammonia. Such relatively low temperature and low pressure conditions can be employed.
[0019]
[Liquid flow conditions]
Temperature: less than 100 ° C, preferably 20-90 ° C
Pressure: Normal pressure or less (any pressure that can maintain the liquid phase)
Flow rate: SV1 to 100 hr −1 , preferably 10 to 50 hr −1
Moreover, since the decomposition rate of hydrogen peroxide will become small when the pH of waste water is acidic less than 7, it is preferable that it is pH 7 or more, especially pH 7-13.
[0020]
In the hydrogen peroxide decomposition apparatus 1, hydrogen peroxide in the raw water is decomposed into water and oxygen, and oxygen gas is discharged out of the system.
[0021]
The treated water of the hydrogen peroxide decomposing apparatus 1 contains almost no hydrogen peroxide and ammonia remains, but in the present invention, this water is introduced into the ammonia volatilization tower 2 to volatilize the ammonia in the water. To remove.
[0022]
Any known method such as a stripping method or an evaporation method (including a distillation method) can be adopted as the method for removing ammonia by volatilization, but the operating conditions are a low temperature of less than 100 ° C. and normal pressure or less. The low-pressure conditions are preferably employed. Specifically, the following method can be employed.
[0023]
(i) Stripping with air, nitrogen gas or the like at a water temperature of 20 ° C. or more and a gas-liquid ratio (G / L) of 1000 to 5000 times.
(ii) Stripping with steam at a water temperature of 60 ° C. or higher with a steam volume / throughput ratio of 5 to 20%.
(iii) Distillation is performed at a water temperature of 60 ° C. or more with a steam amount / treatment amount ratio of 5 to 60% and a reflux ratio of 1 to 7.
[0024]
The treated water from which ammonia has been volatilized and removed in this manner is discharged out of the system.
[0025]
The volatilized ammonia gas can be condensed and recovered as necessary, and can be effectively used for wafer cleaning and the like.
[0026]
The ammonia gas may be decomposed and removed by catalytic air oxidative decomposition.
[0027]
As the catalyst used for the catalytic air oxidative decomposition, the same catalyst as the hydrogen peroxide decomposition catalyst (excluding activated carbon) can be used.
[0028]
【Example】
The present invention will be described more specifically with reference to the following examples.
[0029]
Example 1
A synthetic waste water of ammonia nitrogen: 1250 mg / L, hydrogen peroxide: 6000 mg / L, pH 10.5 was prepared, and this was used as raw water. First, a cobalt peroxide-supported zeolite catalyst (cobalt supported amount 2.5 wt%, average A column packed with 60 mL of particle size 2 mm) was passed under the following conditions.
[0030]
[Liquid flow conditions]
Temperature: 20 ° C
Pressure: Normal pressure Flow rate: 370 mL / hr (SV = 6 hr −1 )
The hydrogen peroxide concentration in the effluent was 2 mg / L or less, and the ammoniacal nitrogen concentration was 1200 mg / L.
[0031]
1000 mL of this effluent is put into a volatilization column in which an acrylic resin column having an inner diameter of 50 mm and a height of 1500 mm is filled with glass beads having a diameter of 3 mm, and air is blown from the lower part with a diffusion tube at a speed of 50 NL / min (G / L = 3000). Double) and treated for 1 hour (water temperature 60 ° C.). The concentration of ammoniacal nitrogen remaining in the treated water was 60 mg / L.
[0032]
On the other hand, the average concentration of ammonia in the volatile gas generated in the volatile treatment was 600 ppm (volume ratio).
[0033]
After this volatilized gas was heated to 330 ° C., an oxidation catalyst tower (a reaction tower in which a stainless steel reaction tower having an inner diameter of 50 mm was filled with 150 mL of 0.5 wt% platinum-supported γ-alumina oxidation catalyst) was used at a superficial velocity (SV) of 20000 hr. After aeration at -1 , a reduction catalyst tower (a reaction tower in which a stainless steel reaction tower having an inner diameter of 50 mm was filled with 500 mL of a vanadium-titania reduction catalyst) was aerated at a superficial velocity (SV) of 6000 hr- 1 .
[0034]
The obtained treatment gas had an ammonia concentration of 1 ppm (volume ratio) or less and an NO x concentration of 10 ppm (volume ratio) or less.
[0035]
Example 2
A synthetic waste water of ammonia nitrogen: 2000 mg / L, hydrogen peroxide: 6000 mg / L, SiO 2 : 2 mg / L, pH 11.0 was prepared. Using this as raw water, first, 0.5 wt% platinum-supported titania catalyst ( The solution was passed through a column packed with 60 mL of an average particle size of 1.5 mm under the following conditions.
[0036]
[Liquid flow conditions]
Temperature: 60 ° C
Pressure: Normal pressure flow rate: 1200 mL / hr (SV = 30 hr −1 )
The hydrogen peroxide concentration in the effluent was 2 mg / L or less, and the ammoniacal nitrogen concentration was 1800 mg / L.
[0037]
1000 mL of this treatment liquid was concentrated by 1.8 times by performing a simple distillation operation at 100 ° C. using a 2 L branch flask.
[0038]
The concentration of ammoniacal nitrogen in the obtained condensed water was 3900 mg / L, and the SiO 2 concentration was 1 mg / L or less. The concentration of ammoniacal nitrogen in the concentrated water was 60 mg / L.
[0039]
【The invention's effect】
As detailed above, according to the method for treating wastewater containing hydrogen peroxide and ammonia of the present invention,
(1) Hydrogen peroxide and ammonia in waste water can be safely and efficiently treated under relatively low temperature and low pressure operating conditions.
(2) Maintenance management is easier than biological treatment, and the installation area of the apparatus can be reduced and sludge is not generated.
(3) Addition of chemicals is unnecessary.
(4) Ammonia can be recovered and used effectively.
Etc. are produced.
[Brief description of the drawings]
FIG. 1 is a system diagram showing an embodiment of a method for treating wastewater containing hydrogen peroxide and ammonia according to the present invention.
[Explanation of symbols]
1 Hydrogen peroxide decomposition equipment 2 Ammonia volatilization tower

Claims (3)

過酸化水素とアンモニアとを含む排水を、20℃以上〜100℃未満かつ常圧以下〜液相が維持できる圧力の条件下で、触媒有効成分として、白金、パラジウム、ルテニウム、ロジウム、インジウム、イリジウム、銀、金、コバルト、銅、ニッケル及びタングステン、並びにこれらの金属の水不溶性又は水難溶性の化合物から選ばれる1種又は2種以上を担体に担持した触媒と接触させて該排水中の過酸化水素を分解し、過酸化水素の分解により発生する酸素ガスを系外へ排出した後、20℃以上〜100℃未満かつ常圧以下の条件下でアンモニアを揮散させて除去することを特徴とする過酸化水素とアンモニアとを含む排水の処理法。 Platinum, palladium, ruthenium, rhodium, indium, iridium as an active catalyst component under the conditions of 20 ° C. to less than 100 ° C. and under normal pressure to a pressure capable of maintaining a liquid phase of waste water containing hydrogen peroxide and ammonia In contact with a catalyst carrying one or more selected from silver, gold, cobalt, copper, nickel and tungsten, and a water-insoluble or poorly water-soluble compound of these metals on a carrier. After decomposing hydrogen and discharging oxygen gas generated by decomposition of hydrogen peroxide to the outside of the system , the ammonia is volatilized and removed under conditions of 20 ° C. or higher and lower than 100 ° C. and normal pressure or lower. To treat wastewater containing hydrogen peroxide and ammonia. 過酸化水素とアンモニアとを含む排水を、20℃以上〜100℃未満かつ常圧以下〜液相が維持できる圧力の条件下で、触媒有効成分として、白金、パラジウム、ルテニウム、ロジウム、インジウム、イリジウム、銀、金、コバルト、銅、ニッケル及びタングステン、並びにこれらの金属の水不溶性又は水難溶性の化合物から選ばれる1種又は2種以上を担体に担持した触媒と接触させて該排水中の過酸化水素を分解し、過酸化水素の分解により発生する酸素ガスを系外へ排出した後、20℃以上〜100℃未満かつ常圧以下の条件下でアンモニアを揮散、凝縮させて回収することを特徴とする過酸化水素とアンモニアとを含む排水の処理法。 Platinum, palladium, ruthenium, rhodium, indium, iridium as an active catalyst component under the conditions of 20 ° C. to less than 100 ° C. and under normal pressure to a pressure capable of maintaining a liquid phase of waste water containing hydrogen peroxide and ammonia In contact with a catalyst carrying one or more selected from silver, gold, cobalt, copper, nickel and tungsten, and a water-insoluble or poorly water-soluble compound of these metals on a carrier. After decomposing hydrogen and discharging oxygen gas generated by the decomposition of hydrogen peroxide to the outside of the system , ammonia is volatilized and condensed under conditions of 20 ° C. to less than 100 ° C. and normal pressure or less. A method for treating wastewater containing hydrogen peroxide and ammonia. 過酸化水素とアンモニアとを含む排水を、20℃以上〜100℃未満かつ常圧以下〜液相が維持できる圧力の条件下で、触媒有効成分として、白金、パラジウム、ルテニウム、ロジウム、インジウム、イリジウム、銀、金、コバルト、銅、ニッケル及びタングステン、並びにこれらの金属の水不溶性又は水難溶性の化合物から選ばれる1種又は2種以上を担体に担持した触媒と接触させて該排水中の過酸化水素を分解し、過酸化水素の分解により発生する酸素ガスを系外へ排出した後、20℃以上〜100℃未満かつ常圧以下の条件下でアンモニアを揮散させ、揮散後のアンモニアを触媒と接触させて分解することを特徴とする過酸化水素とアンモニアとを含む排水の処理法。 Platinum, palladium, ruthenium, rhodium, indium, iridium as an active catalyst component under the conditions of 20 ° C. to less than 100 ° C. and under normal pressure to a pressure capable of maintaining a liquid phase of waste water containing hydrogen peroxide and ammonia In contact with a catalyst carrying one or more selected from silver, gold, cobalt, copper, nickel and tungsten, and a water-insoluble or poorly water-soluble compound of these metals on a carrier. After decomposing hydrogen and discharging oxygen gas generated by decomposition of hydrogen peroxide to the outside of the system , ammonia is volatilized under conditions of 20 ° C. to less than 100 ° C. and below normal pressure, and the ammonia after volatilization is catalyzed. A method for treating wastewater containing hydrogen peroxide and ammonia, which is decomposed by contacting with water.
JP22309398A 1998-08-06 1998-08-06 Treatment of wastewater containing hydrogen peroxide and ammonia Expired - Fee Related JP4066527B2 (en)

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