JP2000051871A - Method for treating drainage containing hydrogen peroxide and ammonia - Google Patents

Method for treating drainage containing hydrogen peroxide and ammonia

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Publication number
JP2000051871A
JP2000051871A JP10223093A JP22309398A JP2000051871A JP 2000051871 A JP2000051871 A JP 2000051871A JP 10223093 A JP10223093 A JP 10223093A JP 22309398 A JP22309398 A JP 22309398A JP 2000051871 A JP2000051871 A JP 2000051871A
Authority
JP
Japan
Prior art keywords
ammonia
hydrogen peroxide
drainage
containing hydrogen
catalyst
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
Application number
JP10223093A
Other languages
Japanese (ja)
Other versions
JP4066527B2 (en
Inventor
Toshiji Nakahara
敏次 中原
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries 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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP22309398A priority Critical patent/JP4066527B2/en
Publication of JP2000051871A publication Critical patent/JP2000051871A/en
Application granted granted Critical
Publication of JP4066527B2 publication Critical patent/JP4066527B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To treat hydrogen peroxide and ammonia in drainage safely and efficiently in operation conditions of a relatively low temperature and a low pressure by a method in which after the drainage being contacted with a catalyst to decompose hydrogen peroxide in the drainage, ammonia is evaporated and removed. SOLUTION: Drainage containing hydrogen peroxide (H2O2) and ammonia (NH3) is introduced into a hydrogen peroxide decomposition apparatus 1 to conduct the catalytic decomposition of the hydrogen peroxide. As the apparatus 1, a fluidized bed type reaction is preferable, conditions of a relatively low temperature and a low pressure can be adopted, the hydrogen peroxide in the drainage is decomposed into water and oxygen, and the oxygen gas is discharged outside a system. Next, the treated water is introduced into an ammonia evaporation column 2, and the ammonia is evaporated at a low temperature and under a low pressure to be removed. The treated water after the evaporation of ammonia is discharged outside the system, and the ammonia gas is condensed as required to be recovered and used effectively.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[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。
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】[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。
2. Description of the Related Art Waste water containing hydrogen peroxide and ammonia is discharged from a semiconductor manufacturing process. Hydrogen peroxide in this wastewater is applied to COD Mn and needs to be decomposed. Ammonia causes eutrophication in rivers, lakes and seas, and must be treated.

【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。
Hitherto, as a method for removing only ammonia in wastewater, there is a method using biological treatment. However, the method using biological treatment generates sludge; it is difficult to maintain and control; Requires equipment footprint;
There are disadvantages such as.

【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。
[0004] Hydrogen peroxide in 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 to obtain a stable water quality.

【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)。
As a method for solving the above problems and simultaneously efficiently decomposing and removing hydrogen peroxide and ammonia in wastewater, the present applicant has previously proposed a method for decomposing both components using a noble metal-supported catalyst. (JP-A-5-269475).
No.).

【0006】[0006]

【発明が解決しようとする課題】特開平5−26947
5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。
Problems to be Solved by the Invention
The catalytic cracking method using a noble metal-supported catalyst disclosed in Japanese Patent No. 5 requires operation at high temperature and high pressure, and has a problem of high initial cost.

【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。
[0007] The present invention solves such a problem, and provides hydrogen peroxide and ammonia which can safely and efficiently treat hydrogen peroxide and ammonia in wastewater under relatively low temperature and low pressure operating conditions. It is an object of the present invention to provide a method for treating wastewater containing.

【0008】[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触媒と接触させて該排水中の過酸化
水素を分解した後、アンモニアを揮散させて除去するこ
とを特徴とする。
According to the method for treating wastewater containing hydrogen peroxide and ammonia according to the present invention, the wastewater containing hydrogen peroxide and ammonia is brought into contact with a catalyst to decompose the hydrogen peroxide in the wastewater. After that, ammonia is volatilized and removed.

【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。
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 a high temperature and high pressure operating condition is not required and the temperature is 100 ° C. Lower temperature, less than normal pressure,
Catalytic cracking can be performed under low pressure operating conditions.

【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。
Ammonia remaining in the waste water after decomposing and removing hydrogen peroxide can be easily removed by volatilization. The volatilized ammonia may be condensed, collected and reused, or may be decomposed by catalytic air oxidation.

【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。
When ammonia is volatilized prior to catalytic decomposition of hydrogen peroxide in order to catalytically decompose only hydrogen peroxide in the wastewater, oxygen gas is simultaneously generated by decomposition of hydrogen peroxide, and thermal efficiency And a gas-explosive mixed gas of oxygen gas and ammonia gas is generated.

【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。
According to the present invention, safe and efficient processing can be performed by removing ammonia by catalytic decomposition and removing ammonia by volatilization.

【0013】[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。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail with reference to the drawings.

【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。
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.

【0015】過酸化水素(H22)及びアンモニア(N
3)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。
[0015] Hydrogen peroxide (H 2 O 2 ) and ammonia (N
The wastewater (raw water) containing H 3 ) is first introduced into the hydrogen peroxide decomposer 1 to perform catalytic decomposition of hydrogen peroxide.

【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。
As the catalytic cracking apparatus 1, it is preferable to use a fixed bed type reaction tower filled with a catalyst.

【0017】本発明において、触媒としては、活性炭が
挙げられるが、それ以外でも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。このような活性炭や担持触媒は、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活性
炭や担持触媒の粒径は、通常0.2〜10mm、特に
0.5〜5mm程度であることが好ましい。
In the present invention, examples of the catalyst include activated carbon, and other than that, platinum, palladium, ruthenium, rhodium, indium,
Iridium, silver, gold, cobalt, copper, nickel and tungsten, and water-insoluble or poorly water-soluble compounds of these metals, specifically, cobalt monoxide, cobalt peroxide, nickel monoxide, ruthenium dioxide, rhodium trioxide , One or more oxides selected from oxides such as palladium monoxide, iridium dioxide, cupric oxide, and tungsten dioxide are supported on a carrier such as alumina, activated carbon, titanium oxide, zirconia, zeolite, and other synthetic resins. There is also a thing that did. The amount of the metal and / or its compound supported in the supported catalyst is usually 0.05 to 25% by weight, preferably 0.5 to 10% by weight of the weight of the carrier. Such activated carbons and supported catalysts can be used in various forms such as spherical, pellet, columnar, crushed pieces, honeycomb, powder, and the like. The particle size is usually preferably 0.2 to 10 mm, particularly preferably about 0.5 to 5 mm.

【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。
The conditions for passing the liquid 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, since only hydrogen peroxide is decomposed without decomposing ammonia, the following relatively low temperature and low pressure conditions can be employed.

【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10〜50
hr-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。
[Liquid passing conditions] Temperature: less than 100 ° C., preferably 20 to 90 ° C. Pressure: Normal pressure or less (a pressure that can maintain the liquid phase is sufficient) Flow rate: SV1 to 100 hr −1 , preferably 10 to 10 50
hr -1 Further , if the pH of the waste water is acidic below 7, the decomposition rate of hydrogen peroxide is reduced, so that the pH is 7 or more, especially pH 7 to
It is preferably 13.

【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。
In the hydrogen peroxide decomposition apparatus 1, hydrogen peroxide in raw water is decomposed into water and oxygen, and oxygen gas is discharged out of the system.

【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。
The treated water of the hydrogen peroxide decomposing apparatus 1 contains almost no hydrogen peroxide and remains ammonia. In the present invention, this water is introduced into the ammonia volatilization tower 2 and the ammonia in the water is removed. Is stripped off.

【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。
As the method for stripping off and removing ammonia, all known methods such as a stripping method and an evaporation method (including a distillation method) can be employed. The operating conditions are as follows: less than 100 ° C., normal pressure It is preferable to employ the following low-temperature and low-pressure conditions, and specifically, the following method can be employed.

【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5〜6
0%、還流比1〜7で蒸留する。
(I) The gas-liquid ratio (G /
L) Stripping is performed at 1000 to 5000 times with air, nitrogen gas or the like. (ii) At a water temperature of 60 ° C. or more, a steam amount / processing amount ratio of 5 to 20.
Strip with steam in%. (iii) At a water temperature of 60 ° C. or more, a steam amount / processing amount ratio of 5 to 6
Distill at 0%, reflux ratio 1-7.

【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。
The treated water from which the ammonia has been volatilized and removed in this way is discharged out of the system.

【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。
The vaporized ammonia gas can be condensed and collected as needed, and can be effectively used for wafer cleaning and the like.

【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。
This ammonia gas may be decomposed and removed by catalytic air oxidative decomposition.

【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。
As the catalyst used for the catalytic air oxidative decomposition, the same catalyst (except for activated carbon) similar to the above-mentioned hydrogen peroxide decomposition catalyst can be used.

【0028】[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。
The present invention will be described more specifically with reference to the following examples.

【0029】実施例1 アンモニア性窒素:1250mg/L、過酸化水素:6
000mg/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。
Example 1 Ammoniacal nitrogen: 1250 mg / L, hydrogen peroxide: 6
000 mg / L, synthetic wastewater having a pH of 10.5 was prepared, and this was used as raw water. First, a column packed with 60 mL of a zeolite catalyst carrying cobalt peroxide (cobalt carrying amount 2.5% by weight, average particle diameter 2 mm) was packed into a column filled with The solution was passed under the conditions.

【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。
[Pouring conditions] Temperature: 20 ° C. Pressure: normal pressure Flow rate: 370 mL / hr (SV = 6 hr −1 ) The concentration of hydrogen peroxide in the effluent is 2 mg / L or less, and the concentration of ammonia nitrogen is 1200 mg / L. Met.

【0031】この流出液1000mLを、内径50m
m、高さ1500mmのアクリル樹脂カラムに直径3m
m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、60
mg/Lであった。
1000 mL of this effluent was used for an inner diameter of 50 m.
m, 3m diameter on 1500mm height acrylic resin column
m into a volatilization tower filled with glass beads, and blow air from the bottom through a diffuser at a rate of 50 NL / min (G /
(L = 3000 times) for 1 hour (water temperature 60 ° C.). The concentration of ammonia nitrogen remaining in the water after the treatment is 60
mg / L.

【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。
On the other hand, the average concentration of ammonia in the volatilized gas generated in the volatilization treatment was 600 ppm (volume ratio).

【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。
After the gaseous gas was heated to 330 ° C., it was placed in a stainless steel reaction tower having an inner diameter of 50 mm.
After aerating velocity (SV) of 20,000 hr -1 , a vanadium-titania-based reduction catalyst was passed through a stainless steel reaction tower having an inner diameter of 50 mm. A reaction tower filled with 500 mL) was aerated at a superficial velocity (SV) of 6000 hr -1 .

【0034】得られた処理ガスのアンモニア濃度は1p
pm(容量比)以下、NOX濃度は10ppm(容量
比)以下であった。
The ammonia concentration of the obtained processing gas is 1 p
pm (volume ratio) or less, NO X concentration was less than 10 ppm (by volume).

【0035】実施例2 アンモニア性窒素:2000mg/L、過酸化水素:6
000mg/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。
Example 2 Ammoniacal nitrogen: 2000 mg / L, hydrogen peroxide: 6
000 mg / L, SiO 2 : 2 mg / L, pH 11.0
Of synthetic wastewater, and this was used as raw water.
The solution was passed through a column packed with 60 mL of a weight-% platinum-supported titania catalyst (average particle size: 1.5 mm) under the following conditions.

【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。
[Pouring conditions] Temperature: 60 ° C. Pressure: normal pressure Flow rate: 1200 mL / hr (SV = 30 hr −1 ) The concentration of hydrogen peroxide in the effluent is 2 mg / L or less, and the concentration of ammonia nitrogen is 1800 mg / L. Met.

【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。
The treated solution (1000 mL) was concentrated 1.8-fold by simple distillation at 100 ° C. using a 2-L branched flask.

【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60
mg/Lであった。
The concentration of ammonia nitrogen in the obtained condensed water was 3900 mg / L, and the concentration of SiO 2 was 1 mg / L or less. The ammonia nitrogen concentration in the concentrated water is 60
mg / L.

【0039】[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、 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。 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。 薬剤の添加が不要である。 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。
As described above in detail, according to the method for treating wastewater containing hydrogen peroxide and ammonia according to the present invention, the hydrogen peroxide and ammonia in the wastewater can be treated at a relatively low temperature.
Safe and efficient processing under low pressure operating conditions. It is easier to maintain and manage than biological treatment, and the equipment installation area can be reduced, and no sludge is generated. No drug addition is required. Ammonia can be recovered and used effectively. And the like.

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

【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。
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.

【符号の説明】[Explanation of symbols]

1 過酸化水素分解装置 2 アンモニア揮散搭 1 Hydrogen peroxide decomposition equipment 2 Ammonia volatilization tower

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 1/58 C02F 1/58 P Fターム(参考) 4D037 AA13 AB11 AB12 BB06 BB09 CA09 CA11 4D038 AA08 AB26 AB29 BA02 BB02 BB03 BB15 BB16 BB20 4D050 AA13 AB33 AB35 BA08 BB09 BC01 BC06 CA02 CA03 4G069 AA02 AA03 BA01B BA04B BA07B BB02B BB04B BB20B BC50B BC54B BC67B BC75B CA05 CA07 CA08 CA11 CA17 DA06 EA02Y EB18Y ZA03B──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI theme coat ゛ (reference) C02F 1/58 C02F 1/58 PF term (reference) 4D037 AA13 AB11 AB12 BB06 BB09 CA09 CA11 4D038 AA08 AB26 AB29 BA02 BB02 BB03 BB15 BB16 BB20 4D050 AA13 AB33 AB35 BA08 BB09 BC01 BC06 CA02 CA03 4G069 AA02 AA03 BA01B BA04B BA07B BB02B BB04B BB20B BC50B BC54B BC67B BC75B CA05 CA07 CA08 CA11 CA17 DA06 EA02

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 過酸化水素とアンモニアとを含む排水を
触媒と接触させて該排水中の過酸化水素を分解した後、
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。
1. After contacting a waste water containing hydrogen peroxide and ammonia with a catalyst to decompose hydrogen peroxide in the waste water,
A method for treating wastewater containing hydrogen peroxide and ammonia, which comprises stripping and removing ammonia.
【請求項2】 過酸化水素とアンモニアとを含む排水を
触媒と接触させて該排水中の過酸化水素を分解した後、
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。
2. After contacting a wastewater containing hydrogen peroxide and ammonia with a catalyst to decompose hydrogen peroxide in the wastewater,
A method for treating wastewater containing hydrogen peroxide and ammonia, wherein ammonia is volatilized, condensed, and recovered.
【請求項3】 過酸化水素とアンモニアとを含む排水を
触媒と接触させて該排水中の過酸化水素を分解した後、
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。
3. After contacting a wastewater containing hydrogen peroxide and ammonia with a catalyst to decompose hydrogen peroxide in the wastewater,
A method for treating wastewater containing hydrogen peroxide and ammonia, wherein ammonia is volatilized, and the ammonia after volatilization is brought into contact with a catalyst to be decomposed.
JP22309398A 1998-08-06 1998-08-06 Treatment of wastewater containing hydrogen peroxide and ammonia Expired - Fee Related JP4066527B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP22309398A JP4066527B2 (en) 1998-08-06 1998-08-06 Treatment of wastewater containing hydrogen peroxide and ammonia

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP22309398A JP4066527B2 (en) 1998-08-06 1998-08-06 Treatment of wastewater containing hydrogen peroxide and ammonia

Publications (2)

Publication Number Publication Date
JP2000051871A true JP2000051871A (en) 2000-02-22
JP4066527B2 JP4066527B2 (en) 2008-03-26

Family

ID=16792733

Family Applications (1)

Application Number Title Priority Date Filing Date
JP22309398A Expired - Fee Related JP4066527B2 (en) 1998-08-06 1998-08-06 Treatment of wastewater containing hydrogen peroxide and ammonia

Country Status (1)

Country Link
JP (1) JP4066527B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001276619A (en) * 2000-03-29 2001-10-09 Kurabo Ind Ltd Method of decomposing hydrogen peroxide and pretreatment method for electrochemical analysis of liquid to be inspected containing hydrogen peroxide
KR20020064678A (en) * 2001-02-02 2002-08-09 가부시키가이샤 닛폰 쇼쿠바이 Process For Treating Waste Water and Apparatus Therefor
JP2014104410A (en) * 2012-11-27 2014-06-09 Japan Organo Co Ltd Processing unit of ammonia inclusion discharge water and processing method of ammonia inclusion discharge water

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001276619A (en) * 2000-03-29 2001-10-09 Kurabo Ind Ltd Method of decomposing hydrogen peroxide and pretreatment method for electrochemical analysis of liquid to be inspected containing hydrogen peroxide
KR20020064678A (en) * 2001-02-02 2002-08-09 가부시키가이샤 닛폰 쇼쿠바이 Process For Treating Waste Water and Apparatus Therefor
JP2014104410A (en) * 2012-11-27 2014-06-09 Japan Organo Co Ltd Processing unit of ammonia inclusion discharge water and processing method of ammonia inclusion discharge water

Also Published As

Publication number Publication date
JP4066527B2 (en) 2008-03-26

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