JPS60227885A - Treatment of hydrazine-containing waste water - Google Patents

Treatment of hydrazine-containing waste water

Info

Publication number
JPS60227885A
JPS60227885A JP8500184A JP8500184A JPS60227885A JP S60227885 A JPS60227885 A JP S60227885A JP 8500184 A JP8500184 A JP 8500184A JP 8500184 A JP8500184 A JP 8500184A JP S60227885 A JPS60227885 A JP S60227885A
Authority
JP
Japan
Prior art keywords
hydrazine
hypochlorite
waste water
concentration
water
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.)
Pending
Application number
JP8500184A
Other languages
Japanese (ja)
Inventor
Noriharu Sasaki
佐々木 典令
Yoichi Kato
洋一 加藤
Haruki Miura
三浦 治樹
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.)
Hitachi Plant Construction Co Ltd
Hitachi Plant Technologies Ltd
Original Assignee
Hitachi Plant Construction Co Ltd
Hitachi Plant Technologies 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 Hitachi Plant Construction Co Ltd, Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Construction Co Ltd
Priority to JP8500184A priority Critical patent/JPS60227885A/en
Publication of JPS60227885A publication Critical patent/JPS60227885A/en
Pending legal-status Critical Current

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  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PURPOSE:To treat waste water without having remaining hypochlorite with less chemical consumption by mixing the treated water with preliminary waste water having the concn. of hydrazine below effluent standard and treating the same with the hypochlorite. CONSTITUTION:The concn. of the hydrazine in the inlet of a reaction vessel 1 is measured and the waste water is stored in a storage tank 12 if the measured value is below the effluent standard. The waste water is introduced into the vessel 1 and the hypochlorite is added approximately at the equiv. of the hydrazine to the waste water to oxidize and decompose the hydrazine if the measured value is above the effluent standard. The treated water is mixed with the preliminary waste water in order to decompose the remaining hypochlorite under the treatment. The treatment without having the remaining hypochlorite is thus executed.

Description

【発明の詳細な説明】 本発明は、ヒドラジンを含有する廃水の処理装置に係り
、特に次亜塩素酸塩を用いてヒドラジンを分解する処理
方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a treatment device for wastewater containing hydrazine, and particularly to a treatment method for decomposing hydrazine using hypochlorite.

火力発電所や原子力発電所では、定期点検等のためにプ
ラン1〜の稼働を停止する場合Gこ、機器や配管の腐食
防止のため、ヒドラジンを添加した純水で満たしておく
。そして、プラントの起動時には、この水を放流するが
、ヒドラジンはCODとして検出されるので、処理する
必要がある。そのため、従来、このようなヒドラジン含
有廃水に次亜塩素酸ナトリウムを添加して、廃水中のヒ
ドラジンを酸化分解する方法が行われていた。この方法
では、ヒドラジンに対して過剰の次亜塩素酸す1ヘリウ
ムを添加し、処理水中の次亜塩素酸すトリウムの濃度を
残留塩素計で測定し、残留塩素濃度か0.2〜i pp
mの範囲となるように次亜塩素酸ナトリウムの添加量を
制御していた。しかし、この方法では処理水中に次亜塩
素酸すトリウムか残留し、これが新たな水質汚染の原因
となる。それというのは、次亜塩素酸塩は毒性か強いの
で、微量残留しても、水中生物に被害を及ばず懸念があ
るからである。従って、次亜塩素酸塩を残留させない処
理方法の開発が望まれている。しかしなから次亜塩素酸
塩の濃度の測定器の精度や検出限界には制限があり、次
亜塩素酸塩の残留の問題を解消することはできなかった
At thermal power plants and nuclear power plants, when the operation of Plan 1~ is stopped for periodic inspection etc., the water is filled with pure water containing hydrazine to prevent corrosion of equipment and piping. When the plant is started up, this water is discharged, but since hydrazine is detected as COD, it must be treated. Therefore, a conventional method has been to add sodium hypochlorite to such hydrazine-containing wastewater to oxidize and decompose the hydrazine in the wastewater. In this method, an excess of sodium hypochlorite is added to hydrazine, and the concentration of sodium hypochlorite in the treated water is measured using a residual chlorine meter.
The amount of sodium hypochlorite added was controlled to be within the range of m. However, with this method, sodium hypochlorite remains in the treated water, which causes new water pollution. This is because hypochlorite is highly toxic, so even if it remains in trace amounts, there is concern that it will not harm aquatic life. Therefore, it is desired to develop a treatment method that does not leave hypochlorite residue. However, there are limits to the accuracy and detection limits of the hypochlorite concentration measuring instruments, and the problem of residual hypochlorite could not be resolved.

本発明の目的は、前記の従来技術の欠点を解消し、処理
水中に次亜塩素酸塩を残留することなくヒドラジンを分
解することができ、ヒドラジン濃度の変動が激しい廃水
にも適用しうるヒドラジン含有廃水の処理方法を提供す
ることにある。
The object of the present invention is to solve the above-mentioned drawbacks of the prior art, to provide hydrazine that can decompose hydrazine without leaving hypochlorite in treated water, and that can be applied to wastewater where the hydrazine concentration fluctuates widely. An object of the present invention is to provide a method for treating wastewater containing wastewater.

本発明は、ヒドラジンはCOD源ではあるが、所定濃度
以下であれば、放流光の水中生物に直接被害を及はさな
いことに着目して、次亜塩素酸塩の濃度を測定するので
はなく、ヒドラジン濃度を測定し、所定濃度以上のヒド
ラジンを含む廃水だけを次亜塩素酸塩で処理することに
よって達成されたものである。
The present invention focuses on the fact that although hydrazine is a COD source, as long as it is below a predetermined concentration, the discharged light will not directly harm aquatic organisms, and the concentration of hypochlorite is measured. This was achieved by measuring the hydrazine concentration and treating only wastewater containing hydrazine above a predetermined concentration with hypochlorite.

即ち、本発明によるヒドラジン含有廃水の処理方法は、
反応槽入口のヒドラジン濃度を測定し、この測定値が放
流基準以下である場合には、その廃水を貯槽に貯留させ
、測定値が放流基準以上である場合には、反応槽へ導入
し、次亜塩素酸塩をヒドラジンに対してほぼ反応当量で
添加してヒドラジンを酸化分解させ、反応槽からの処理
水と貯槽からの廃水とを適当な割合で混合することを特
徴とする。
That is, the method for treating hydrazine-containing wastewater according to the present invention is as follows:
The hydrazine concentration at the inlet of the reaction tank is measured, and if the measured value is below the discharge standard, the wastewater is stored in a storage tank, and if the measured value is above the discharge standard, it is introduced into the reaction tank and then The method is characterized in that chlorite is added in approximately the reaction equivalent amount to hydrazine to oxidize and decompose the hydrazine, and treated water from the reaction tank and wastewater from the storage tank are mixed in an appropriate ratio.

本発明方法においては、まず廃水のヒドラジン濃度を測
定し、その測定値が放/M、基準以上である場合に、廃
水を反応槽に導入し、次亜塩素酸塩をほぼ反応当量で添
加する。しかし、処理水中のヒドラジン濃度が10pp
m以下である場合、第1図に示すように次亜塩素酸塩が
残留する。そごで、本発明方法ではヒドラジン濃度の放
流基準、例えば1100pp (CODとして40pp
m)以下の廃水を分離して貯留しておき、これを前記の
次亜塩素酸処理水と混合してヒドラジン濃度を10pp
m以−J=、に調節することによって処理水中に次亜塩
素酸塩が残留しないようにした。
In the method of the present invention, the hydrazine concentration of wastewater is first measured, and if the measured value is above the release/M standard, the wastewater is introduced into a reaction tank and hypochlorite is added in approximately the reaction equivalent amount. . However, the hydrazine concentration in the treated water was 10pp.
m or less, hypochlorite remains as shown in FIG. Therefore, in the method of the present invention, the discharge standard of hydrazine concentration is set, for example, 1100 pp (40 pp as COD).
m) Separate and store the following wastewater and mix it with the hypochlorous acid treated water to reduce the hydrazine concentration to 10pp.
Hypochlorite was prevented from remaining in the treated water by adjusting m to -J=.

反応槽における次亜塩素酸塩注入量の制御は、(1)反
応槽入口のヒドラジン濃度、(2)反応槽出口のヒドラ
ジン濃度及び(3)混合水のヒドラジン濃度のいずれに
基づいてもよい。
The amount of hypochlorite injected into the reaction tank may be controlled based on any of (1) the hydrazine concentration at the reaction tank inlet, (2) the hydrazine concentration at the reaction tank outlet, and (3) the hydrazine concentration in the mixed water.

(1)の場合には、処理水又は混合水のし1′ラジン濃
度か反映されないので、厳格さに欠けるかヒドラジンの
放流基準が緩和である場合には、次亜塩素酸塩の注入量
を少なめにして充分対応することができる。
In the case of (1), the concentration of 1' radine in the treated water or mixed water is not reflected, so if the standards for hydrazine discharge are not strict or the standards for hydrazine discharge are relaxed, the amount of hypochlorite injected may be changed. It is possible to cope with it with a small amount.

第2図には、(2)に基づく制御方式を採用した処理フ
ローシートを示す。この装置において、監視槽1には、
ヒドラジン含有廃水の導入管2、排出管3、バイパス管
4及びヒドラジン濃度計5か接続されている。排出管3
にはハルプロが設けられ、反応槽7に接続され、反応槽
7はヒドラジン濃度計8を設置した管路9を介して混合
槽10に接続されている。バイパス管4にはバルブ11
か設けられ、貯槽12に接続され、貯槽12はポンプ1
3を介して管路14により混合槽10に接続されている
。また、混合槽10には、ヒドラジン濃度計15が設置
されている。反応槽7には、バルブ16を有する次亜塩
素酸塩の供給管17が接続されている。
FIG. 2 shows a processing flow sheet that employs the control method based on (2). In this device, the monitoring tank 1 includes:
An inlet pipe 2, a discharge pipe 3, a bypass pipe 4, and a hydrazine concentration meter 5 are connected to the hydrazine-containing wastewater. Discharge pipe 3
is equipped with a HALPRO and connected to a reaction tank 7, and the reaction tank 7 is connected to a mixing tank 10 via a conduit 9 in which a hydrazine concentration meter 8 is installed. A valve 11 is installed in the bypass pipe 4.
is connected to the storage tank 12, and the storage tank 12 is connected to the pump 1.
3 and is connected to the mixing tank 10 by a conduit 14. Further, a hydrazine concentration meter 15 is installed in the mixing tank 10. A hypochlorite supply pipe 17 having a valve 16 is connected to the reaction tank 7 .

また、ヒドラジン濃度計5ばハルプロ及びバルブ11の
開閉を行う制御器18に接続され、ヒドラジン濃度計8
はバルブ16の開度を調節する制御器19に接続され、
更にヒドラジン濃度計8及びヒドラジン濃度計15はポ
ンプ13を起動又は停止する制御器20に接続されてい
る。
In addition, the hydrazine concentration meter 5 is connected to a controller 18 that opens and closes the HALPRO and the valve 11.
is connected to a controller 19 that adjusts the opening degree of the valve 16,
Further, the hydrazine concentration meter 8 and the hydrazine concentration meter 15 are connected to a controller 20 that starts or stops the pump 13.

この装置を用いて処理を行う場合、ヒドラジン含有水は
導入管2から監視槽1に導入され、ここでヒドラジン濃
度計5により測定した値がヒドラジン濃度の放流基準、
例えば1100pp (COD40ppm)以下である
とき、制御器18によりハルプロを閉じ、バルブ11を
開け、バイパス管4を通って貯槽12に一時貯留される
。また、ヒドラジン濃度が放流基準以上である場合には
、バルブ11を閉じ、ハルプロを開け、ヒドラジン含有
廃水は排出管3を通って反応槽7へ導入される。
When performing treatment using this device, hydrazine-containing water is introduced into the monitoring tank 1 from the introduction pipe 2, and the value measured here by the hydrazine concentration meter 5 is the discharge standard for the hydrazine concentration.
For example, when it is below 1100 ppm (COD 40 ppm), the controller 18 closes the HALPRO, opens the valve 11, and temporarily stores it in the storage tank 12 through the bypass pipe 4. Further, when the hydrazine concentration is equal to or higher than the discharge standard, the valve 11 is closed, the HALPRO is opened, and the hydrazine-containing wastewater is introduced into the reaction tank 7 through the discharge pipe 3.

ここで、廃水中のヒドラジンは供給管17から送入され
る次亜塩素酸塩と接触し、窒素と水とに分解される。
Here, the hydrazine in the wastewater comes into contact with the hypochlorite fed through the supply pipe 17 and is decomposed into nitrogen and water.

この処理水は管路9を通って混合槽10に導入される。This treated water is introduced into a mixing tank 10 through a pipe 9.

その際、管路9に設けたヒドラジン濃度計8で処理水の
ヒドラジン濃度を測定し、この出力信号に応して制御器
19によってバルブ1Gの開度を調節し、ヒドラジン濃
度が放流基準、例えば1100pp以下で、かつ次亜塩
素酸塩か残留しない、ヒドラジン濃度lQppm以上の
範囲に制御する。
At that time, the hydrazine concentration of the treated water is measured with the hydrazine concentration meter 8 installed in the pipe line 9, and the opening degree of the valve 1G is adjusted by the controller 19 according to this output signal, so that the hydrazine concentration is determined according to the discharge standard, e.g. The hydrazine concentration is controlled within a range of 1100 ppm or less and no hypochlorite remains, and the hydrazine concentration is 1Q ppm or more.

更に、原水中のヒドラジン濃度が急激な変動をした場合
等、ヒドラジン濃度計8の測定値がlOppm以下とな
る場合には、制御器20によりポンプ13を起動して貯
槽12に貯留しであるヒドラジン含有廃水を混合槽10
に供給してヒドラジン濃度計15によって測定されるヒ
ドラジン濃度が10ppm以上になるように制御する。
Furthermore, if the hydrazine concentration in the raw water changes rapidly, and the measured value of the hydrazine concentration meter 8 becomes lOppm or less, the controller 20 starts the pump 13 to remove the hydrazine stored in the storage tank 12. Mixing tank 10 containing wastewater
The hydrazine concentration is controlled such that the hydrazine concentration measured by the hydrazine concentration meter 15 is 10 ppm or more.

第2図に示した装置では、前記の(2)に基づく制御方
式を採用しており、この場合には、反応槽における制御
は最も確実である。しかし、貯槽中の予備廃水のヒドラ
ジン濃度が不明のときは、その混合割合を決める手段が
必要となり、混合割合は貯水量とは無関係に決定される
ので、その調整に難点がある。
The apparatus shown in FIG. 2 employs the control method based on (2) above, and in this case, control in the reaction tank is most reliable. However, when the hydrazine concentration of the preliminary wastewater in the storage tank is unknown, a means for determining the mixing ratio is required, and since the mixing ratio is determined regardless of the amount of water stored, there are difficulties in adjusting it.

第3図に示した装置は、前記の(3)に基づく制御方式
を採用したものであり、貯槽12の貯水量に応して制御
を行うことができる。この装置では、混合槽10に設け
たヒドラジン濃度側15の測定値が放流基準以下で、か
つ10ppm以」二になるように、制御器21によって
バルブ16の開度及び/又はポンプ13 (又はバルブ
)が調節される。貯槽12には液面計22が設置され、
制御器21に接続されている。貯槽12における貯水量
が少ない場合には、反応槽における次亜塩素酸塩の注入
量を若干少な目にし、予備水の混合割合も下げる。逆に
、貯水量が多いときは、次亜塩素酸塩注入量を若干多め
にし、予備水の混合割合を上げればよい。
The device shown in FIG. 3 employs the control method based on the above (3), and can perform control according to the amount of water stored in the storage tank 12. In this device, the controller 21 controls the opening degree of the valve 16 and/or the pump 13 (or ) is adjusted. A liquid level gauge 22 is installed in the storage tank 12,
It is connected to the controller 21. When the amount of water stored in the storage tank 12 is small, the amount of hypochlorite injected into the reaction tank is slightly reduced, and the mixing ratio of reserve water is also lowered. On the other hand, when there is a large amount of water stored, the amount of hypochlorite injected may be slightly increased and the mixing ratio of reserve water may be increased.

このような制御によって、主として予備水のヒドラジン
濃度に起因して、混合水のヒドラジン濃度が」−昇する
傾向にあれば、次亜塩素酸塩の注入量を増大させ、ヒド
ラジンが減少する傾向にあれば、次亜塩素酸塩の注入量
を減少させる制御回路を設けるのが更に好ましい。
With such control, if the hydrazine concentration in the mixed water tends to increase, mainly due to the hydrazine concentration in the reserve water, the injection amount of hypochlorite is increased, and hydrazine tends to decrease. It is further preferred to provide a control circuit to reduce the amount of hypochlorite injection, if any.

本発明によれば、反応槽中では次亜塩素酸塩とヒ[ラジ
ンとをほぼ当量で反応させるので、次亜塩素酸塩、ヒド
ラジンともに低い水準に抑えることができる。そして、
ヒドラジン濃度の変動や制御のタイムラグによる処理水
中の残留次亜塩素酸塩を分解させるため、処理水をヒド
ラジン濃度が放流基準以下の予備廃水と混合し、混合水
中の次亜塩素酸塩をヒドラジンと反応させることができ
るので、放流水中に次亜塩素酸塩を確実に残留させない
。また、従来の反応当量、全量処理に比べて、次亜塩素
酸塩の消費量が少なくてすむ。
According to the present invention, since hypochlorite and hydrazine are reacted in approximately equivalent amounts in the reaction tank, both hypochlorite and hydrazine can be suppressed to low levels. and,
In order to decompose residual hypochlorite in the treated water due to fluctuations in hydrazine concentration and time lag in control, the treated water is mixed with preliminary wastewater whose hydrazine concentration is below the discharge standard, and the hypochlorite in the mixed water is mixed with hydrazine. reaction to ensure that no hypochlorite remains in the effluent. In addition, the amount of hypochlorite consumed can be reduced compared to conventional reaction equivalent and total amount treatments.

次に、図面に基づいて本発明を詳述するか、本発明はこ
れに限定されるものではない。
Next, the present invention will be explained in detail based on the drawings, but the present invention is not limited thereto.

実施例 ヒドラジン濃度が200〜500ppmの間で変動する
原水を第2図に示した装置を用い、次亜塩素酸塩として
次亜塩素酸ナトリウムを用いて処理した結果、混合槽出
口のヒドラジン濃度は15〜90ppmであり、次亜塩
素酸ナトリウムは残留しなかった。
Example Raw water with a hydrazine concentration varying between 200 and 500 ppm was treated with sodium hypochlorite as the hypochlorite using the equipment shown in Figure 2. As a result, the hydrazine concentration at the outlet of the mixing tank was It was 15 to 90 ppm, and no sodium hypochlorite remained.

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

第1図は処理水中のヒドラジン濃度と次亜塩素酸ナトリ
ウムの濃度との関係図、第2図は本発明方法を実施する
装置の一実施態様を示すフローシート、第3図は本発明
方法を実施する装置の別の実施態様を示すフローシート
である。 5.8.15・・・ヒドラジン濃度計、7・・・・反応
槽、10・・・混合槽、12・・・・貯槽、18,19
,20.21・・・制御器、22・・・液面計 特許出願人 ・ 日立プラン)・建設株式会社
Fig. 1 is a diagram showing the relationship between the hydrazine concentration and the sodium hypochlorite concentration in treated water, Fig. 2 is a flow sheet showing an embodiment of an apparatus for implementing the method of the present invention, and Fig. 3 is a diagram showing the relationship between the concentration of hydrazine and the concentration of sodium hypochlorite in treated water. 1 is a flow sheet illustrating another embodiment of the apparatus for implementation. 5.8.15... Hydrazine concentration meter, 7... Reaction tank, 10... Mixing tank, 12... Storage tank, 18, 19
, 20.21...Controller, 22...Liquid level gauge Patent applicant/Hitachi Plan)/Kensetsu Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 四)ヒドラジンを含有する廃水を次亜塩素酸塩と接触さ
せてヒドラジンを分解するヒドラジン含有廃水の処理方
法において、反応槽入口のヒドラジン濃度を測定し、こ
の測定値が放流基準以下である場合には、その廃水を貯
槽に貯留させ、測定値が放流基準辺]−である場合には
、反応槽へ導入し、次亜塩素酸塩をヒドラジンに対して
ほぼ反応当量で添加してヒドラジンを酸化分解させ、反
応槽からの処理水と貯槽からの廃水とを適当な2;す合
で混合することを特徴とするヒドラジン含有廃水の処理
方法。
4) In a method for treating hydrazine-containing wastewater in which hydrazine-containing wastewater is brought into contact with hypochlorite to decompose hydrazine, the hydrazine concentration at the inlet of the reaction tank is measured, and if this measured value is below the discharge standard, The wastewater is stored in a storage tank, and if the measured value is at the discharge standard level -, it is introduced into the reaction tank and hypochlorite is added in an approximately reaction equivalent amount to hydrazine to oxidize the hydrazine. A method for treating hydrazine-containing wastewater, which comprises decomposing the water and mixing the treated water from a reaction tank and the wastewater from a storage tank in an appropriate amount.
JP8500184A 1984-04-26 1984-04-26 Treatment of hydrazine-containing waste water Pending JPS60227885A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8500184A JPS60227885A (en) 1984-04-26 1984-04-26 Treatment of hydrazine-containing waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8500184A JPS60227885A (en) 1984-04-26 1984-04-26 Treatment of hydrazine-containing waste water

Publications (1)

Publication Number Publication Date
JPS60227885A true JPS60227885A (en) 1985-11-13

Family

ID=13846423

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8500184A Pending JPS60227885A (en) 1984-04-26 1984-04-26 Treatment of hydrazine-containing waste water

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JP (1) JPS60227885A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010099542A (en) * 2008-10-21 2010-05-06 Sumitomo Metal Mining Co Ltd Method for decomposing away ammonia nitrogen and apparatus for the same
JP2016141868A (en) * 2015-02-04 2016-08-08 三菱重工環境・化学エンジニアリング株式会社 Waste heat recovery apparatus, power generating system, and waste heat recovery method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010099542A (en) * 2008-10-21 2010-05-06 Sumitomo Metal Mining Co Ltd Method for decomposing away ammonia nitrogen and apparatus for the same
JP2016141868A (en) * 2015-02-04 2016-08-08 三菱重工環境・化学エンジニアリング株式会社 Waste heat recovery apparatus, power generating system, and waste heat recovery method
WO2016125649A1 (en) * 2015-02-04 2016-08-11 三菱重工環境・化学エンジニアリング株式会社 Exhaust heat recovery device, power generation system, and exhaust heat recovery method

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