JPH1133583A - Bulking controlling agent of activated sludge and control method - Google Patents

Bulking controlling agent of activated sludge and control method

Info

Publication number
JPH1133583A
JPH1133583A JP9192114A JP19211497A JPH1133583A JP H1133583 A JPH1133583 A JP H1133583A JP 9192114 A JP9192114 A JP 9192114A JP 19211497 A JP19211497 A JP 19211497A JP H1133583 A JPH1133583 A JP H1133583A
Authority
JP
Japan
Prior art keywords
bulking
activated sludge
salt
compound represented
controlling agent
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
JP9192114A
Other languages
Japanese (ja)
Inventor
Tetsuya Ito
哲也 伊藤
Atsuko Narita
敦子 成田
Yasuaki Hashimoto
恭明 橋本
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.)
Nippon Soda Co Ltd
Original Assignee
Nippon Soda Co 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 Nippon Soda Co Ltd filed Critical Nippon Soda Co Ltd
Priority to JP9192114A priority Critical patent/JPH1133583A/en
Publication of JPH1133583A publication Critical patent/JPH1133583A/en
Pending legal-status Critical Current

Links

Classifications

    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00—Technologies for wastewater treatment
    • Y02W10/10—Biological treatment of water, waste water, or sewage

Landscapes

  • Activated Sludge Processes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a bulking controlling agent which prevent the generation of a bulking phenomenon without deterioration of water quality and without retarding the growth of useful flock-forming bacteria in activated sludge processing and a method for controlling bulking. SOLUTION: In a bulking control method of activated sludge, as effective components, at least one of a compound given by formula I, (in which n represents an integer of 0-6, when n is 2 or greater, R can be different from each other; R represents amino, a halogen, hydroxyl, sulfonate, and a 1-40C alkyl or alkenyl or its salt and, as required, a bulking controlling agent of activated sludge containing at least one of a cationic polymer flocculant, an inorganic flocculant, and a clay mineral are added into an aeration tank, a precipitation tank, or return sludge.

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、有機物含有廃水処
理に有効な活性汚泥法において、施設管理上、最大の障
害となる糸状性微生物によるバルキングを防除するため
のバルキング防除剤及びそれを用いたバルキング防除方
法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a bulking control agent for controlling bulking caused by filamentous microorganisms, which is the greatest obstacle in facility management, in an activated sludge method effective for treating organic matter-containing wastewater, and to use the same. It relates to a method for controlling bulking.

【0002】[0002]

【従来の技術】従来、有機物含有廃水の処理方法として
活性汚泥法が広く採用されているが、沈降不良となった
活性汚泥が引き起こすバルキング現象は、活性汚泥法に
おける最大の問題であるといわれている。この原因は、
活性汚泥中の微生物相の生育バランスが崩れ、フロック
形成菌よりも糸状性微生物が優勢となることである。ひ
とたびバルキングが発生すると、活性汚泥が膨化を起こ
し沈殿しにくくなり、沈殿槽において活性汚泥と処理水
との界面を得ることが不可能となって、活性汚泥が流亡
し、環境汚染の原因となっていた。更に、活性汚泥の流
亡により、曝気槽内の活性汚泥のMLSS(曝気槽混合
液内の浮遊物質)濃度が維持されず、廃水中に溶解して
いる有機物の活性汚泥による生物分解が不良となり、よ
り一層の環境汚染をもたらしていた。
2. Description of the Related Art Activated sludge is widely used as a method for treating organic-containing wastewater. However, it is said that the bulking phenomenon caused by activated sludge that has settled poorly is the biggest problem in the activated sludge process. I have. This is because
The growth balance of the microflora in the activated sludge is disrupted, and the filamentous microorganisms predominate over the floc-forming bacteria. Once bulking occurs, the activated sludge swells and becomes difficult to sediment, making it impossible to obtain an interface between the activated sludge and the treated water in the sedimentation tank, causing the activated sludge to run off and causing environmental pollution. I was Furthermore, the runoff of the activated sludge does not maintain the MLSS (suspended matter in the aeration tank mixture) concentration of the activated sludge in the aeration tank, and the biodegradation of the organic matter dissolved in the wastewater by the activated sludge becomes poor. This has caused even more environmental pollution.

【0003】バルキング現象が発生した場合、活性汚泥
の沈降性を大きくする目的で、無機凝集剤や高分子凝集
剤の投入などが行われるのが一般的であり、これら薬剤
が廉価なこともあって、各廃水処理施設において多用さ
れている。更に、廉価な殺菌剤である塩素などを曝気槽
に添加することによるバルキングの防除も行われてい
る。
When the bulking phenomenon occurs, it is common to add an inorganic flocculant or a polymer flocculant in order to increase the sedimentation of activated sludge, and these chemicals may be inexpensive. Therefore, it is frequently used in each wastewater treatment facility. Further, bulking is controlled by adding inexpensive bactericides such as chlorine to the aeration tank.

【0004】[0004]

【発明が解決すべき課題】活性汚泥処理システムへの凝
集剤の添加は、活性汚泥の沈降性悪化を一時的に解決す
るが、単なる応急処置にすぎず、バルキングの原因であ
る糸状性微生物の生育を抑制しているわけではないの
で、バルキングの再発防止には有効でない。また、塩素
等の殺菌剤は選択制がないため、バルキングの原因とな
る糸状性微生物の生育のみならず、活性汚泥の有用な生
物の生育に多大なる悪影響を与え、バルキング防除後に
水質が極端に悪化してしまうことや、有用微生物の死滅
によるバルキングの再発を誘発するという問題があっ
た。本発明の課題は、活性汚泥処理において、水質を悪
化させることなく、さらに、有用なフロック形成菌の生
育を阻害することなく、バルキング現象の発生を防止す
るバルキング防除剤及びバルキング防除方法を提供する
ことにある。
The addition of a flocculant to the activated sludge treatment system temporarily solves the deterioration of the settling property of the activated sludge, but it is only a mere emergency treatment, and the removal of the filamentous microorganisms causing the bulking. It is not effective in preventing the recurrence of bulking because it does not control growth. In addition, since there is no selection system for bactericides such as chlorine, not only the growth of filamentous microorganisms causing bulking, but also the harmful effects on the growth of useful organisms of activated sludge, the water quality becomes extremely poor after bulking control. There has been a problem that it deteriorates and induces a recurrence of bulking due to the death of useful microorganisms. An object of the present invention is to provide a bulking controlling agent and a bulking controlling method for preventing the occurrence of a bulking phenomenon in activated sludge treatment without deteriorating water quality and without inhibiting the growth of useful floc-forming bacteria. It is in.

【0005】[0005]

【課題を解決するための手段】上記課題を解決するため
に、鋭意研究したところ、次の一般式(I)で表される
化合物(式中nは0〜6の整数を表し、nが複数のと
き、Rはそれぞれ異なっていてもよい。Rはアミノ基、
ハロゲン原子、水酸基、スルホン酸基、C1〜40の不
飽和基を有していてもよいアルキル基を表す)又はその
塩の少なくとも1種を有効成分とする活性汚泥のバルキ
ング防除剤が活性汚泥処理におけるバルキング現象の発
生を防止し得ることを見出し、本発明を完成するに至っ
た。
Means for Solving the Problems In order to solve the above-mentioned problems, the present inventors have made intensive studies and found that a compound represented by the following general formula (I) (wherein n represents an integer of 0 to 6; In the formula, R may be different from each other, R is an amino group,
A halogen atom, a hydroxyl group, a sulfonic acid group, or an alkyl group which may have a C1-40 unsaturated group) or a salt thereof as an active ingredient; It has been found that the occurrence of the bulking phenomenon can be prevented, and the present invention has been completed.

【化1】 Embedded image

【0006】すなわち、本発明は、有効成分として、一
般式(I)で示される化合物(式中nは0〜6の整数を
表し、nが複数のとき、Rはそれぞれ異なっていてもよ
い。Rはアミノ基、ハロゲン原子、水酸基、スルホン酸
基、C1〜40の不飽和基を有していてもよいアルキル
基を表す)又はその塩の少なくとも1種を含有する活性
汚泥のバルキング防除剤、一般式(I)で示される化合
物又はその塩の少なくとも1種とカチオン系高分子凝集
剤又は無機凝集剤の少なくとも1種とを含有する活性汚
泥のバルキング防除剤、あるいは、一般式(I)で示さ
れる化合物又はその塩の少なくとも1種とカチオン系高
分子凝集剤又は無機凝集剤の少なくとも1種と粘土鉱物
の少なくとも1種とを含有する活性汚泥のバルキング防
除剤に関する。また、本発明は、上記のいずれかのバル
キング防除剤を曝気槽、沈殿層又は返送汚泥に添加する
ことを特徴とする活性汚泥のバルキング防除方法に関す
る。
That is, in the present invention, as an active ingredient, a compound represented by the general formula (I) (wherein n represents an integer of 0 to 6, and when n is plural, Rs may be different from each other. R represents an amino group, a halogen atom, a hydroxyl group, a sulfonic acid group, an alkyl group which may have a C1 to 40 unsaturated group) or a salt thereof, and a bulking control agent for activated sludge, A bulking control agent for activated sludge containing at least one kind of the compound represented by the general formula (I) or a salt thereof and at least one kind of a cationic polymer flocculant or an inorganic flocculant, or a compound represented by the general formula (I) The present invention relates to a bulking control agent for activated sludge containing at least one kind of the compound or a salt thereof, at least one kind of cationic polymer flocculant or inorganic flocculant, and at least one kind of clay mineral. The present invention also relates to a method for controlling bulking of activated sludge, characterized by adding any of the above bulking controlling agents to an aeration tank, a sedimentation layer or returned sludge.

【0007】[0007]

【発明の実施の形態】本発明にかかるバルキング防除剤
は、活性汚泥処理システムにおいて用いられるものであ
り、ここで活性汚泥処理システムとは、好気的に廃水を
処理するというシステムであり、標準活性汚泥法のほ
か、その変法といわれているすべての方法を包含する。
BEST MODE FOR CARRYING OUT THE INVENTION The bulking control agent according to the present invention is used in an activated sludge treatment system. Here, the activated sludge treatment system is a system for aerobically treating wastewater. In addition to the activated sludge method, all methods that are said to be variations thereof are included.

【0008】本発明にかかるバルキング防除剤として
は、上記のように、有効成分として、一般式(I)で示
される化合物(式中nは0〜6の整数を表し、nが複数
のとき、Rはそれぞれ異なっていてもよい。Rはアミノ
基、ハロゲン原子、水酸基、スルホン酸基、C1〜40
の不飽和基を有していてもよいアルキル基を表す)又は
その塩の少なくとも1種を含有する活性汚泥のバルキン
グ防除剤、一般式(I)で示される化合物又はその塩の
少なくとも1種とカチオン系高分子凝集剤又は無機凝集
剤の少なくとも1種とを含有する活性汚泥のバルキング
防除剤、あるいは、一般式(I)で示される化合物又は
その塩の少なくとも1種とカチオン系高分子凝集剤又は
無機凝集剤の少なくとも1種と粘土鉱物の少なくとも1
種とを含有するものを挙げることができ、一般式(I)
で示される化合物のみの添加でも十分にバルキング抑制
効果は得られるが、高分子凝集剤、無機凝集剤、粘土鉱
物と併用することにより、化合物添加直後の初期汚泥沈
降性が改善され、またバルキング防除期間が持続すると
いう顕著な効果が期待できる。
As described above, the bulking controlling agent according to the present invention includes, as an active ingredient, a compound represented by the general formula (I) (wherein n is an integer of 0 to 6; R may be different from each other, R may be an amino group, a halogen atom, a hydroxyl group, a sulfonic acid group, C1-40.
Or an alkyl group which may have an unsaturated group), or a bulking controlling agent for activated sludge containing at least one kind of a salt thereof, at least one kind of a compound represented by the general formula (I) or a salt thereof. Activated sludge bulking control agent containing at least one cationic polymer flocculant or inorganic flocculant, or at least one compound represented by formula (I) or a salt thereof and a cationic polymer flocculant Or at least one of inorganic coagulants and at least one of clay minerals
And a compound containing a compound represented by the general formula (I):
Although the bulking inhibitory effect can be sufficiently obtained by the addition of only the compound represented by, the initial sludge settling property immediately after the compound addition is improved by using the polymer flocculant, the inorganic flocculant, and the clay mineral together, and the bulking control A remarkable effect that the period lasts can be expected.

【0009】本発明において、一般式(I)のRで表さ
れる置換基としては、アミノ基、塩素、臭素、ヨウ素、
フッ素などのハロゲン原子、水素基、スルホン酸基、メ
チル基、エチル基、プロピル基、イソプロピル基、ブチ
ル基、ter−ブチル基、sec−ブチル基、アリル
基、プロパギル基などの炭素数1〜40の二重結合又は
三重結合を1つ以上有していても良いアルキル基を表
す。水酸基、スルホン酸基の場合はその塩も本化合物に
含まれる。塩としてはナトリウム、カリウム、リチウム
などの通常用いられる金属が挙げられる。置換基数は0
〜6であり、複数個のときは、置換基はそれぞれ異なっ
ていてもよい。化合物の具体的な例としては、1,2−
ナフトキノン、1,2−ナフトキノン−4−スルホン酸
ナトリウム、1,4−ナフトキノン、2−アミノ−3−
クロロ−1,4−ナフトキノン、2,3−ジクロロ−
1,4−ナフトキノン、2−メチル−1,4−ナフトキ
ノン、2−ヒドロキシ−1,4−ナフトキノン、5−ヒ
ドロキシ−1,4−ナフトキノン、2−メチル−5−ヒ
ドロキシ−1,4−ナフトキノン、5,8−ジヒドロキ
シ−1,4−ナフトキノン、ビタミンK1などを挙げる
ことができる。これらの化合物は、単独又は数種を組み
合わせて使用することができる。
In the present invention, the substituent represented by R in the general formula (I) includes an amino group, chlorine, bromine, iodine,
C1-C40 such as halogen atoms such as fluorine, hydrogen groups, sulfonic acid groups, methyl groups, ethyl groups, propyl groups, isopropyl groups, butyl groups, ter-butyl groups, sec-butyl groups, allyl groups, and propargyl groups. Represents an alkyl group which may have one or more double bonds or triple bonds. In the case of a hydroxyl group or a sulfonic acid group, salts thereof are also included in the present compound. Examples of the salt include commonly used metals such as sodium, potassium and lithium. The number of substituents is 0
To 6, and when there are a plurality of substituents, the substituents may be different from each other. Specific examples of the compound include 1,2-
Naphthoquinone, 1,2-naphthoquinone-4-sodium sulfonate, 1,4-naphthoquinone, 2-amino-3-
Chloro-1,4-naphthoquinone, 2,3-dichloro-
1,4-naphthoquinone, 2-methyl-1,4-naphthoquinone, 2-hydroxy-1,4-naphthoquinone, 5-hydroxy-1,4-naphthoquinone, 2-methyl-5-hydroxy-1,4-naphthoquinone, 5,8-dihydroxy-1,4-naphthoquinone, vitamin K1 and the like can be mentioned. These compounds can be used alone or in combination of several kinds.

【0010】本発明において、カチオン系高分子凝集剤
としては、ポリアクリル酸エステル系、ポリメタクリル
酸エステル系、ビニルホルムアミド系、ポリアクリルア
ミド系、ポリアミン系、ジシアンジアミド系高分子凝集
剤を例示することができる。また、無機凝集剤として
は、硫酸アルミニウム、塩化第2鉄等を、粘土鉱物とし
ては、セピオライト、バーミキュライト、アタパルジャ
イト等をそれぞれ例示することができる。
In the present invention, examples of the cationic polymer flocculant include polyacrylate, polymethacrylate, vinylformamide, polyacrylamide, polyamine and dicyandiamide polymer flocculants. it can. Examples of the inorganic coagulant include aluminum sulfate and ferric chloride, and examples of the clay mineral include sepiolite, vermiculite, and attapulgite.

【0011】上記のバルキング剤は、活性汚泥処理シス
テムの任意の場所に添加できるが、曝気槽への添加が最
もバルキング抑制に効果がある。曝気槽への添加方法
は、連続的に添加する方法や、1回/日で2〜3回にわ
けて添加する方法が考えられ、いずれの方法でも自由に
選択できる。また、バルキング発生の程度によっては、
一回のみの添加でも十分なバルキング抑制効果が期待で
きる。また、添加に先立ち、pHや曝気強度の調整な
ど、日常行っている施設の運転管理方法の変更は全く必
要なく、非常に簡単な添加条件でバルキングの抑制効果
が得られる。
The above-mentioned bulking agent can be added to any place in the activated sludge treatment system, but the addition to the aeration tank is most effective in suppressing bulking. As a method of adding to the aeration tank, a method of adding continuously or a method of adding twice or three times per day can be considered, and any method can be freely selected. Also, depending on the degree of bulking,
A sufficient suppression of bulking can be expected with only one addition. Further, prior to the addition, there is no need to change the operation management method of the facility on a daily basis, such as adjusting the pH or the aeration intensity, and the effect of suppressing bulking can be obtained under very simple addition conditions.

【0012】一般式(I)で示される化合物は、通常、
粉体として用いるが、水などに溶解させ、液剤としても
使用できる。粉剤とする場合、上記化合物を曝気槽の総
容量に対し、1〜200mg/l程度、好ましくは、2
〜50mg/l程度添加することで、バルキングの原因
糸状性微生物の生育を抑制することができる。また、沈
殿槽から活性汚泥が流亡しているときには、粘土鉱物や
カチオン系高分子凝集剤又は無機凝集剤の1種又は2種
以上と混ぜ合わせても使用できる。粘土鉱物、無機凝集
剤は、曝気槽総容量に対して、10〜200mg/l程
度、また、高分子凝集剤は、1〜50mg/l程度、好
ましくは、10〜20mg/l程度の添加量が適当であ
る。
The compound represented by the general formula (I) is usually
Although used as a powder, it can be dissolved in water or the like and used as a liquid agent. When a powder is used, the above compound is used in an amount of about 1 to 200 mg / l, preferably
By adding about 50 mg / l, the growth of filamentous microorganisms that cause bulking can be suppressed. Further, when activated sludge is flowing out of the settling tank, it can be used by mixing with one or more of clay mineral, cationic polymer flocculant or inorganic flocculant. The amount of the clay mineral and the inorganic coagulant is about 10 to 200 mg / l, and the amount of the polymer coagulant is about 1 to 50 mg / l, preferably about 10 to 20 mg / l, based on the total volume of the aeration tank. Is appropriate.

【0013】本発明のバルキング防除剤を添加すると、
汚泥の沈降性の改善、活性汚泥中の糸状性微生物の生育
数の減少、糸状性微生物の糸状体の切断、折れ曲がり、
ねじれなどが、添加後数日間で観察できる。しかも、こ
のとき、フロックを形成している有用な微生物や原生動
物の生育への悪影響は全く観察されないため、良好な水
質を得ることができる。このように、本発明によると、
活性汚泥に悪影響を与えることなく、良質な水質を得な
がら、バルキング防除が可能となる。
When the bulking control agent of the present invention is added,
Improvement of sedimentation of sludge, decrease in the growth number of filamentous microorganisms in activated sludge, cutting and bending of filamentous filamentous microorganisms,
Twist and the like can be observed several days after the addition. Moreover, at this time, no adverse effects on the growth of useful microorganisms and protozoa forming flocs are observed, so that good water quality can be obtained. Thus, according to the present invention,
It is possible to control bulking while obtaining good water quality without adversely affecting activated sludge.

【0014】[0014]

【実施例】以下に、実施例を掲げて本発明をさらに具体
的に説明するが、本発明の技術的範囲はこれら実施例に
限定されるものではない。 (バルキングの発生)曝気槽(21)と沈殿槽(0.5
1)が分離している培養装置に、人工合成廃水(グルコ
ース870mg/l、ペプトン250mg/l、塩化ナ
トリウム300mg/l、リン酸二カリウム39mg/
l、硝酸アンモニウム43mg/l)を連続的に供給
し、活性汚泥を培養した。合成廃水の流入量1l/日、
MLSS濃度2,000mg/l、室温20〜25℃の
条件で糸状性バルキングを発生させ、以下の実験を行っ
た。なお、このとき発生していた糸状性微生物は、TY
PE021N、スフェロチルス ナタンス、TYPE1
701、TYPE1702であった。(Eikelbo
om D.H.Filamentous organi
sms observed in activated
sludge.Water Research vo
l.9:365−388(1975)に記載された方法
で、糸状性微生物の識別を行った。)。
EXAMPLES Hereinafter, the present invention will be described more specifically with reference to examples, but the technical scope of the present invention is not limited to these examples. (Generation of bulking) Aeration tank (21) and sedimentation tank (0.5)
In the culture device from which 1) is separated, artificially synthesized wastewater (glucose 870 mg / l, peptone 250 mg / l, sodium chloride 300 mg / l, dipotassium phosphate 39 mg / l)
l, ammonium nitrate 43 mg / l) was continuously supplied, and the activated sludge was cultured. 1 l / day of synthetic wastewater inflow,
Filamentous bulking was generated under the conditions of MLSS concentration of 2,000 mg / l and room temperature of 20 to 25 ° C., and the following experiment was performed. The filamentous microorganisms generated at this time were TY.
PE021N, Spherothylus natansu, TYPE1
701 and TYPE 1702. (Eikelbo
omD. H. Filamentous organi
sms observed in activated
sludge. Water Research vo
l. 9: 365-388 (1975), the filamentous microorganisms were identified. ).

【0015】(バルキング抑制効果の判定)バルキング
抑制効果の判定は、シリンダーに3時間(180分間)
静置した時の活性汚泥の沈降性(SV180と表す)、
顕微鏡観察による糸状性微生物の生育判断(非常に多い
=+++>++>+>±=非常に少ない)、曝気槽のp
H、処理水の濁り(濁っている=+、透明である=
−)、原生動物の個体数への影響(影響あり=あり、影
響なし=なし)で行った。
(Judgment of bulking suppression effect) Judgment of bulking suppression effect is carried out for 3 hours (180 minutes)
Sedimentation of activated sludge when settled (expressed as SV180),
Judgment of the growth of filamentous microorganisms by microscopic observation (very much = ++++++++ ±± very little), p of aeration tank
H, turbidity of treated water (cloudy = +, transparent =
-), The effect on the protozoan population (affected = present, no effect = none).

【0016】(実施例1〜8)糸状性微生物によりバル
キングが発生している活性汚泥に、表1の各実施例に示
した化合物を曝気槽に対して10mg/l・回の割合で
2回添加した。添加後、連続培養を続け、試験開始から
4日目にバルキング抑制効果を判定した。また、何も添
加しないものを対照とした。その結果、対照区の汚泥沈
降性は、SV180値=94%であったが、各実施例の
化合物添加区では、汚泥の沈降性が改善され、糸状性微
生物の生育数も減少した。また、曝気槽水のpHは、対
照区とほとんど同じであり、沈殿槽の濁りも観察され
ず、原生動物の個体数の減少もなかった。
(Examples 1 to 8) Compounds shown in Examples of Table 1 were applied twice to activated sludge, in which bulking was caused by filamentous microorganisms, at a rate of 10 mg / l.times. Was added. After the addition, continuous culture was continued, and the effect of suppressing bulking was determined on the fourth day from the start of the test. A control without any addition was used as a control. As a result, the sludge settling property of the control plot was SV180 = 94%, but in the compound-added plots of the examples, the sludge sedimentation property was improved, and the number of filamentous microorganisms grown was also reduced. The pH of the aeration tank water was almost the same as that of the control group, no turbidity was observed in the settling tank, and the number of protozoa was not reduced.

【0017】[0017]

【表1】 [Table 1]

【0018】[0018]

【発明の効果】本発明のバルキング防除剤を曝気槽に添
加することにより、フロックを形成している有用な微生
物の生育に悪影響を与えることなく、糸状性微生物の生
育数を減少させることができ、その結果、汚泥の沈降性
も大幅に改善される。
By adding the bulking control agent of the present invention to an aeration tank, the number of filamentous microorganisms that can grow can be reduced without adversely affecting the growth of useful microorganisms forming flocs. As a result, the sedimentation of the sludge is greatly improved.

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 一般式(I)で示される化合物又はその
塩の少なくとも1種を有効成分として含有することを特
徴とする活性汚泥のバルキング防除剤 【化1】 (式中nは0〜6の整数を表し、nが複数のとき、Rは
それぞれ異なっていてもよい。Rはアミノ基、ハロゲン
原子、水酸基、スルホン酸基、C1〜40の不飽和基を
有していてもよいアルキル基を表す)
1. A bulking control agent for activated sludge, characterized by containing at least one compound represented by the general formula (I) or a salt thereof as an active ingredient. (In the formula, n represents an integer of 0 to 6, and when n is plural, Rs may be different from each other. R represents an amino group, a halogen atom, a hydroxyl group, a sulfonic acid group, a C1 to 40 unsaturated group. Represents an alkyl group which may be present)
【請求項2】 一般式(I)で示される化合物又はその
塩の少なくとも1種とカチオン系高分子凝集剤又は無機
凝集剤の少なくとも1種とを有効成分として含有するこ
とを特徴とする活性汚泥のバルキング防除剤
2. Activated sludge comprising as an active ingredient at least one compound represented by the general formula (I) or a salt thereof and at least one cationic polymer flocculant or inorganic flocculant. Bulking control agent
【請求項3】 一般式(I)で示される化合物又はその
塩の少なくとも1種と、カチオン系高分子凝集剤又は無
機凝集剤の少なくとも1種と、粘土鉱物の少なくとも1
種とを有効成分として含有することを特徴とする活性汚
泥のバルキング防除剤
3. A compound represented by the general formula (I) or at least one salt thereof, at least one cationic polymer flocculant or inorganic flocculant, and at least one clay mineral.
Activated sludge bulking controlling agent characterized by containing seeds as an active ingredient
【請求項4】 請求項1〜3のいずれか記載のバルキン
グ防除剤を曝気槽、沈殿層又は返送汚泥に添加すること
を特徴とする活性汚泥のバルキング防除方法
4. A method for controlling bulking of activated sludge, which comprises adding the bulking control agent according to claim 1 to an aeration tank, a sedimentation layer, or returned sludge.
JP9192114A 1997-07-17 1997-07-17 Bulking controlling agent of activated sludge and control method Pending JPH1133583A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9192114A JPH1133583A (en) 1997-07-17 1997-07-17 Bulking controlling agent of activated sludge and control method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9192114A JPH1133583A (en) 1997-07-17 1997-07-17 Bulking controlling agent of activated sludge and control method

Publications (1)

Publication Number Publication Date
JPH1133583A true JPH1133583A (en) 1999-02-09

Family

ID=16285910

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9192114A Pending JPH1133583A (en) 1997-07-17 1997-07-17 Bulking controlling agent of activated sludge and control method

Country Status (1)

Country Link
JP (1) JPH1133583A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003523821A (en) * 2000-02-17 2003-08-12 ガーネット、インコーポレイティッド Methods for controlling the growth of zoological and aquatic plants

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003523821A (en) * 2000-02-17 2003-08-12 ガーネット、インコーポレイティッド Methods for controlling the growth of zoological and aquatic plants

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