JPS5990695A - Treatment of waste water - Google Patents
Treatment of waste waterInfo
- Publication number
- JPS5990695A JPS5990695A JP19903282A JP19903282A JPS5990695A JP S5990695 A JPS5990695 A JP S5990695A JP 19903282 A JP19903282 A JP 19903282A JP 19903282 A JP19903282 A JP 19903282A JP S5990695 A JPS5990695 A JP S5990695A
- Authority
- JP
- Japan
- Prior art keywords
- reaction tank
- nox
- range
- orp
- value
- 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
Links
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は、し尿、家畜糞尿、水産加工廃水等を無希釈の
まま、めるいは極低希釈のままで、しかも単一槽でNH
4−N除去とNoX−N除去とを高効率で行う方法に関
する。DETAILED DESCRIPTION OF THE INVENTION The present invention enables human waste, livestock manure, fisheries processing wastewater, etc. to be processed without dilution, and with very low dilution, and in a single tank.
The present invention relates to a method for highly efficiently removing 4-N and NoX-N.
通常の活性汚泥法の適用範囲を超えた高濃度廃液(例え
ば、し尿、家畜糞尿、水産加工廃水など〕を直接無希釈
のまま生物処理する場合、空気供給下の単一反応槽にお
いて生活虫境条件が全く異質の硝化菌(好気性状態で増
殖)と脱窒菌(嫌気性状態で増殖)の協同作用でNH4
−N(アンモニア性窒素)除去とN0X−N (No2
−NとNO3−Nの和)除去が同時に行われる。しかし
、異質の生理特性を有する両者の活性度を最大限に高め
NH4−N除去とNOX −N除去を高効率で並存せし
める安定操作方法が従来不明であった。When directly undiluted biological treatment of high-concentration waste liquid (e.g. human waste, livestock manure, fisheries processing wastewater, etc.) that exceeds the scope of application of the normal activated sludge method, living insects can be grown in a single reaction tank under air supply. NH4 is produced by the cooperative action of nitrifying bacteria (proliferates in aerobic conditions) and denitrifying bacteria (propagates in anaerobic conditions), both of which have completely different conditions.
-N (ammoniac nitrogen) removal and NOX-N (No2
-N and NO3-N) removal is performed simultaneously. However, a stable operation method that maximizes the activity of both substances, which have different physiological characteristics, and allows NH4-N removal and NOX-N removal to coexist with high efficiency has not been known so far.
本発明は、このNH4−N除去とN0X−N除去を単一
槽で高効率で実現し得る方法を提供するもので、通常の
活性汚泥法の適用範囲を超えた高濃度窒素含有廃液を直
接無希釈あるいは極低希釈で生物処理する方法において
、空気供給下の単一反応槽でNH4−N除去と同時にN
oX−N除去を高効率で行うために反応楕円液の酸化還
元電位を0〜100 mV(07)ZVを除く〕の範囲
に設定することを特徴とする廃水処理法に関するもので
ある。The present invention provides a method that can achieve highly efficient NH4-N removal and NOX-N removal in a single tank, and directly treats high-concentration nitrogen-containing waste liquid, which is beyond the scope of application of the normal activated sludge method. In the method of biological treatment using no dilution or extremely low dilution, NH4-N can be removed simultaneously in a single reaction tank under air supply.
The present invention relates to a wastewater treatment method characterized by setting the redox potential of the reaction ellipsoid to a range of 0 to 100 mV (excluding 07) ZV in order to remove oX-N with high efficiency.
第1図は本発明方法の一実施態様例を示す図である。FIG. 1 is a diagram showing an example of an embodiment of the method of the present invention.
第1図に示すよう呪高濃度廃液1を直接無希釈処理する
反応槽10において、反応槽混合液中に0RP(酸化還
元電位ノセンサー9を設置して混合液ORB値を連続的
に測定記録してこのORB値が0〜1oomvの範囲に
入るように曝気空気8量の調整を行う(なお、ORPが
この範囲に入ると、NH4−N除去機能を保持する上で
1要なりo値がその好ましい範囲でめる0〈DO(1p
pm tic必然的に制御されるン。As shown in Fig. 1, in a reaction tank 10 that directly processes the high concentration waste liquid 1 without dilution, an ORP (redox potential sensor 9) is installed in the reaction tank mixture to continuously measure and record the mixed liquid ORB value. Then, adjust the amount of aeration air so that this ORB value falls within the range of 0 to 1 oomv (note that when ORP falls within this range, 1 is required to maintain the NH4-N removal function, and the o value is 0〈DO (1p
pm tic necessarily controlled.
なお、図中、2は返送汚泥ライン、6は電動機、4はブ
ロワ−15は曝気装置、6は処理液抜出しラインで、図
示省略の汚泥分離工程へ導かれており、7は排ガス抜出
しラインで必る。In the figure, 2 is a return sludge line, 6 is an electric motor, 4 is a blower, 15 is an aeration device, 6 is a treated liquid extraction line, which leads to the sludge separation process (not shown), and 7 is an exhaust gas extraction line. Must have.
以下、実験例によυ本発明方法を具体的に説明する。The method of the present invention will be specifically explained below using experimental examples.
実験装置(第1図に示すもの) 反応槽10 : 20靜反応塔 塔径1.9m、有効液深7m 曝気装置5:ロータリーアトマイザ− (カップ状の回転体を500 〜600 rpmで回転させ、 カップ内に曝気空気を供給 するもの)を適用。Experimental equipment (as shown in Figure 1) Reaction tank 10: 20 silent reaction tower Tower diameter 1.9m, effective liquid depth 7m Aeration device 5: Rotary atomizer (500 cup-shaped rotating bodies Rotate at ~600 rpm, Supplying aeration air into the cup apply).
径0.45m 高0.675771
対象廃液
無希釈し尿: BOD 8800 ppmTota
l−N 3100 ppm
NH4−N 2600ppm
実験条件
ORP : −50〜+1507′nVで変化処理量:
10n//日
空気量:30〜250 Nrr?/hrで変化液温:2
5〜30℃
第2,3図に、上記の実験で得られたNH4−N除去速
度、NOx、 −N除去速度の検討結果を示す。Diameter 0.45m Height 0.675771 Target waste liquid undiluted human waste: BOD 8800 ppmTota
l-N 3100 ppm NH4-N 2600 ppm Experimental conditions ORP: -50 to +1507'nV change in processing amount:
10n//day air amount: 30-250 Nrr? /hr Changes liquid temperature: 2
5 to 30°C Figures 2 and 3 show the results of the study of the NH4-N removal rate, NOx, and -N removal rate obtained in the above experiment.
なお、第2,6図はORBを+40〜+ 100mVの
範囲としたものでDOは0.4〜1.0ppmであp、
処理液(DNO,−N濃度は100 ppmでおった。In addition, in Figures 2 and 6, ORB is in the range of +40 to +100 mV, and DO is 0.4 to 1.0 ppm, p,
The treatment solution (DNO, -N concentration was 100 ppm.
また、これらの速度は、それぞれ次式で表わされる。Further, these speeds are each expressed by the following equations.
NH4−N除去速度 −dN/dt = kHzBNN
Ox −N除去速度 −dn/dt = k2ZBここ
で、N : NH4−N濃度CI)I)m )、n :
kiOx−N 9度(ppm)、kl;NH4−’N
除去速度恒数、k、: N0X−N除去速度恒数、Z、
: MLIIES濃度(ppm)である。NH4-N removal rate -dN/dt = kHzBNN
Ox -N removal rate -dn/dt = k2ZB, where, N: NH4-N concentration CI)I)m), n:
kiOx-N 9 degrees (ppm), kl; NH4-'N
Removal rate constant, k,: N0X-N removal rate constant, Z,
: MLIIES concentration (ppm).
第4図には、反応塔混仕液ORPとに1 t kZとの
関係を求めた結果を示す。第4図中、11および會印は
NOx −Nを、12および0印はNH4−N 全それ
ぞれ示している。第4図から明らかなように、0RPO
〜100mVでkl p kl値は最大値を示し、10
0tny以上およびomv以下では急激に低下している
。この理由は、(i)ORPが0以下では、高濃度活性
汚泥(10000ppm以上)のフロック内に遊離酸素
が十分に浸透せず、硝化機能に対する活性阻害が生じる
。(!1)ORPが10 rJmV以上では、逆に遊離
酸素の浸透量が過剰となり、No、 −N除去機能に活
性阻害を生じ、混合液中にNo2−Nが大量蓄積するよ
うになり、No2−Nは硝化機能に活性阻害作用がおる
のでNH,−N除去機能が低下することKある。FIG. 4 shows the results of determining the relationship between the reaction tower mixed feed ORP and 1 t kZ. In FIG. 4, marks 11 and 0 indicate NOx-N, and marks 12 and 0 indicate NH4-N, respectively. As is clear from Figure 4, 0RPO
At ~100 mV, the kl p kl value shows a maximum value, and 10
It rapidly decreases above 0 tny and below omv. The reason for this is (i) When ORP is 0 or less, free oxygen does not sufficiently permeate into the flocs of high-concentration activated sludge (10,000 ppm or more), and the nitrification function is inhibited. (!1) When the ORP is 10 rJmV or more, the amount of free oxygen that permeates becomes excessive, inhibiting the activity of the No, -N removal function, and a large amount of No2-N accumulates in the mixed solution, causing the No2 Since -N has an activity-inhibiting effect on the nitrification function, the ability to remove NH and -N may be reduced.
従って、NH4−N除去(酸化)とN0x−N除去(還
元)を並存させる設定領域としてORB値に制限がある
ことが判シ、本発明では上記の実験結果からORB値を
0〜100mVの範囲に選定したものである。この範囲
のORB値で反応槽を運転することにより、1i1H4
−kl除去とIJ’OX−N除去を同時に高効率で行う
ことができる。Therefore, it is clear that there is a limit to the ORB value as a setting range where NH4-N removal (oxidation) and NOx-N removal (reduction) coexist.In the present invention, based on the above experimental results, the ORB value is set within the range of 0 to 100 mV. It was selected as follows. By operating the reactor in this range of ORB values, 1i1H4
-Kl removal and IJ'OX-N removal can be performed simultaneously with high efficiency.
第1図は本発明方法の一実施態様例を示す図、第2〜4
図は本発明の実験で得られた結果を示す図である。
復代理人 内 1) 明
復代理人 萩 原 亮 −
見2図
反応塔内活性〉5泥H(kg)Figure 1 is a diagram showing an example of an embodiment of the method of the present invention, Figures 2 to 4
The figure is a diagram showing the results obtained in an experiment of the present invention. Sub-agent 1) Meifuku agent Ryo Hagiwara - Figure 2 Activity inside the reaction column> 5 mud H (kg)
Claims (1)
液を直接無希釈あるいは極低希釈で生物処理する方法に
おいて、空気供給下の単一反応槽でNH4−N除去と同
時にN0x−IJ線除去高効率で行うために反応槽内液
の酸化還元電位を〇〜100mV (DmVを除く)の
範囲に設定することを特徴とする廃水処理法。In a method of directly biologically treating high-concentration nitrogen-containing waste liquid, which exceeds the scope of application of the normal activated sludge method, with no dilution or extremely low dilution, NH4-N is removed in a single reaction tank under air supply, and NOx-IJ lines are removed at the same time. A wastewater treatment method characterized by setting the oxidation-reduction potential of the reaction tank liquid in the range of 0 to 100 mV (excluding DmV) in order to perform removal with high efficiency.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP19903282A JPS5990695A (en) | 1982-11-15 | 1982-11-15 | Treatment of waste water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP19903282A JPS5990695A (en) | 1982-11-15 | 1982-11-15 | Treatment of waste water |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS5990695A true JPS5990695A (en) | 1984-05-25 |
Family
ID=16400975
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP19903282A Pending JPS5990695A (en) | 1982-11-15 | 1982-11-15 | Treatment of waste water |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5990695A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS62163798A (en) * | 1986-01-13 | 1987-07-20 | Meidensha Electric Mfg Co Ltd | Treatment of waste water |
JPS62286597A (en) * | 1986-06-03 | 1987-12-12 | Sumitomo Jukikai Envirotec Kk | Biological denitrification of raw excretion |
JP2008501500A (en) * | 2004-06-02 | 2008-01-24 | オテヴェ・ソシエテ・アノニム | Water treatment method using bioreactor and corresponding apparatus in which the speed of the air continuously injected into the reactor is adjusted |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5763195A (en) * | 1980-10-02 | 1982-04-16 | Kubota Ltd | Water treatment for denitrification |
-
1982
- 1982-11-15 JP JP19903282A patent/JPS5990695A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5763195A (en) * | 1980-10-02 | 1982-04-16 | Kubota Ltd | Water treatment for denitrification |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS62163798A (en) * | 1986-01-13 | 1987-07-20 | Meidensha Electric Mfg Co Ltd | Treatment of waste water |
JPS62286597A (en) * | 1986-06-03 | 1987-12-12 | Sumitomo Jukikai Envirotec Kk | Biological denitrification of raw excretion |
JP2008501500A (en) * | 2004-06-02 | 2008-01-24 | オテヴェ・ソシエテ・アノニム | Water treatment method using bioreactor and corresponding apparatus in which the speed of the air continuously injected into the reactor is adjusted |
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