JPS59186696A - Treatment of waste water - Google Patents

Treatment of waste water

Info

Publication number
JPS59186696A
JPS59186696A JP6189883A JP6189883A JPS59186696A JP S59186696 A JPS59186696 A JP S59186696A JP 6189883 A JP6189883 A JP 6189883A JP 6189883 A JP6189883 A JP 6189883A JP S59186696 A JPS59186696 A JP S59186696A
Authority
JP
Japan
Prior art keywords
waste water
water
ozone
oxygen
released
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
JP6189883A
Other languages
Japanese (ja)
Inventor
Hiroyuki Hagiwara
萩原 弘之
Kazuo Endo
遠藤 和夫
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.)
Proterial Ltd
Original Assignee
Hitachi Metals 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 Metals Ltd filed Critical Hitachi Metals Ltd
Priority to JP6189883A priority Critical patent/JPS59186696A/en
Publication of JPS59186696A publication Critical patent/JPS59186696A/en
Pending legal-status Critical Current

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  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PURPOSE:To make waste water contg. an excessive org. high polymer flocculating agent non-pollutive by adding a mineral acid to the waste water contg. the org. high polymer flocculating agent to adjust the pH to <=7 and bringing ozone into gas-liquid contact with the waste water for <=10min at a ratio of 1-5wt%. CONSTITUTION:The waste water A contg. an org. high polymer flocculating agent is conducted to a pH adjusting tank 7, where a mineral acid such as a sulfuric acid is added thereto to make the acidic waste water A1 having <=7pH which is then conducted into an aerating tank 1 provided with a diffuser 5 and while the waste water is aerated for a specified time, the water is stagnated therein. The oxygen D from an oxygen feeder 2 is passed through an ozone generator 3 and the resultant ozone E is released from the diffuser 5 by a fan 4 and is brought into contact with the waste water A1 during the stagnation. The water is released as treated water C after the stagnation for a specified time. The waste gas B from the tank 1 is decomposed by a waste gas treating device 6 and is released into the atmosphere. Pure oxygen or dehumidified air is available as the oxygen D to be supplied to the generator 3.

Description

【発明の詳細な説明】 本発明は、排水処理又は汚泥処理等に伴い発生する高分
子電解質を主成分とする高分子凝集剤を含有する排水の
処理法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating wastewater containing a polymer flocculant containing a polymer electrolyte as a main component, which is generated during wastewater treatment or sludge treatment.

従来、下水等の排水に含有している浮遊物は、重力濃縮
又は加圧浮上濃縮等の方法により濃縮した後、有機高分
子凝集剤を添加して凝集をし、脱水処理される。有機高
分子凝集剤は、浮遊物を凝集し脱水を容易とする作用を
有するが、通常は凝集をより促進することを目的として
いる為に過剰量を添加している。その結果、脱水により
分離をする水中に余剰の有機高分子凝集剤が排出される
Conventionally, suspended solids contained in wastewater such as sewage are concentrated by gravity concentration or pressure flotation concentration, and then an organic polymer flocculant is added to cause flocculation and dehydration treatment. The organic polymer flocculant has the effect of flocculating suspended matter and facilitating dehydration, but is usually added in an excessive amount because the purpose is to further promote flocculation. As a result, excess organic polymer flocculant is discharged into the water that is separated by dehydration.

有機高分子凝集剤は元来高い粘性を有するため、有機高
分子凝集剤を含有する排水は発泡し、処理設備周辺の美
観を著しく損う。又、高分子電解質を主成分とする有機
高分子凝集剤は魚貝類に対する毒性をも有するため、有
機高分子凝集剤を含有する排水を活性汚泥等による生物
処理設備に返流した場合、活性汚泥の膨化等に悪影響が
ある。さらに、化学的に合成した有機高分子は生物に対
する毒性を有することから、そのまま大量に河川等の水
域に放流した場合には魚貝類の斃死や植物の生育障害等
の二次公害を引き起す。′↑−年に、下水汚泥等を処理
する目的で使用しているカチオン系高分子凝集剤は、魚
類のエラに付着しその生体機能を損い斃死に致もしめる
急性 本発明は高分子電解質を主成分とする有機高分子凝集剤
を余剰に含有した排水を無害化することを目的とする。
Since organic polymer flocculants inherently have high viscosity, wastewater containing organic polymer flocculants foams, significantly impairing the aesthetic appearance of the surroundings of treatment equipment. In addition, organic polymer flocculants whose main components are polymer electrolytes are also toxic to fish and shellfish, so if wastewater containing organic polymer flocculants is returned to biological treatment equipment using activated sludge, activated sludge This has an adverse effect on swelling, etc. Furthermore, chemically synthesized organic polymers are toxic to living organisms, so if they are released in large quantities into water bodies such as rivers, they cause secondary pollution such as death of fish and shellfish and impaired growth of plants. '↑-In 2013, cationic polymer flocculants used to treat sewage sludge, etc. adhered to the gills of fish, impairing their biological functions and causing death. The purpose is to render harmless wastewater that contains an excess of organic polymer flocculants, the main component of which is

発明の要点は排水とオゾンを接触させて、オゾンの酸化
力により排水中の高分子凝集剤の電荷を失わせ、粘性を
失わせることにある。
The key point of the invention is to bring waste water into contact with ozone, and the oxidizing power of ozone causes the polymer flocculant in the waste water to lose its charge and lose its viscosity.

本弁明の実施例を第1図に示す。有機高分子凝集剤を含
有する排水AをPH調整槽7に導き硫酸等の鉱酸を添加
してPH7以下の酸性排水A1とし、ディ7・、−ザ5
を備えた曝気槽1に導き一定時間の曝気をしつつ滞留す
る。その滞留時に酸素供給装置2かもの酸素D’ltシ
ン発生機3に流通してイ尋られたオゾンEを送風機4で
ディフューザ5カ)ら放出して排水A1と接触をする。
An embodiment of this defense is shown in FIG. The wastewater A containing an organic polymer flocculant is led to the pH adjustment tank 7, and a mineral acid such as sulfuric acid is added thereto to make the wastewater A1 acidic with a pH of 7 or less.
The water is introduced into an aeration tank 1 equipped with an air conditioner and retained therein while being aerated for a certain period of time. When the ozone E is retained, it is distributed to the oxygen supply device 2 and the oxygen generator 3, and the ozone E is released from the diffuser 5 by the blower 4 and comes into contact with the waste water A1.

一定時間の滞留後は、処理水Cとして放流する。曝気槽
1カ)もの杉トガスBは、廃ガス処理装置乙により分解
され大気へ放散される。オゾン発生装置6に供給する酸
素りは、純酸素又は除湿された空気も利用できる。
After residence for a certain period of time, it is discharged as treated water C. Aeration tank 1) Cedar gas B is decomposed by waste gas treatment device B and released into the atmosphere. As the oxygen supplied to the ozone generator 6, pure oxygen or dehumidified air can be used.

曝気槽1の容積は、排水量なもととしオソ゛ンEとの接
触効率等の要因から決めらね、るカベオン°ンEと排水
Aとの接触時間10分間未満で充分である。
The volume of the aeration tank 1 is determined based on factors such as the amount of drainage and the contact efficiency with the ozone E, but a contact time of less than 10 minutes between the caveon E and the wastewater A is sufficient.

オゾンは強い酸化力を有する気体で、オソ゛ン発生機に
より容易に製造できる特徴を有すること力・ら、従来工
業原料の漂白、下水処理設備の脱臭。
Ozone is a gas with strong oxidizing power and can be easily produced using an ozone generator.Ozone is also used for bleaching conventional industrial raw materials and deodorizing sewage treatment equipment.

高度処理としてのCOD低下、脱色、殺菌、脱臭等広範
囲に使用されている。
It is widely used as advanced treatment for COD reduction, decolorization, sterilization, deodorization, etc.

オゾンによる有機物の酸化機構をま、オソ゛ンの中心の
酸素原子が相対的に電子欠乏状態にあることから、多重
結合を有する有機物と反応してこれを分解又は形態の変
化を引き起す結果、脱色、脱臭。
In contrast to the oxidation mechanism of organic matter by ozone, since the oxygen atom at the center of ozone is relatively electron-deficient, it reacts with organic matter having multiple bonds, decomposing it or causing a change in form, resulting in decolorization, Deodorizing.

殺菌等の作用が得られる。Effects such as sterilization can be obtained.

一方、アニオン性又はカチオン性高分子凝集剤は多数の
電解基な有し、これを水中に溶解させることにより高分
子イオンと低分子イオン(対イオン)に解離する。解離
した高分子イオンは高い粘性を生じ、これを汚泥等の懸
濁粒子を含有する液中に添加すると懸濁粒子の保持する
電荷を中和し粒子間に架橋することにより凝集効果を発
揮するのである。
On the other hand, anionic or cationic polymer flocculants have a large number of electrolytic groups, and when dissolved in water, they dissociate into polymer ions and low molecular ions (counter ions). Dissociated polymer ions produce high viscosity, and when added to a liquid containing suspended particles such as sludge, it neutralizes the charge held by the suspended particles and creates a coagulation effect by creating bridges between particles. It is.

表1に高分子凝集剤のオゾン処理結果を示す。Table 1 shows the results of ozone treatment of the polymer flocculant.

この表1は、有機高分子凝集剤の娘度を0.25wt係
とし5分間処理した場合であり、オゾン濃度は2%wt
%とじ、粘度は回転式粘度計により測定した。
Table 1 shows the case where the daughterness of the organic polymer flocculant was set to 0.25wt and the treatment was carried out for 5 minutes, and the ozone concentration was 2%wt.
% binding and viscosity were measured using a rotational viscometer.

表1によれば、5分間のオゾン曝気により有機高分子凝
集剤はその高い粘性を失い水と同等の粘度を示す。また
、有機高分子凝集剤の粘性及び身性の指標となるカチオ
ン族は、/・イモロックIViP−175I−(の場合
、処理前に4.5 (meq/S’ )であったものが
オゾン処理後には0.4 (meq/ f )にまで低
下し、著しくその活性を失う。(カチオン匿の分析は、
ボンビニル硫酸カリウムを用いたコロイド滴定法による
。)表  1 表  2 又、下水汚泥を処理する際に、脱水機より排出される廟
機高分子#:巣剤を含有する下水汚泥σ)脱水濾液のオ
ゾン処理結果を表2に示す。下水汚泥中の固形分は3w
t%、高分子凝集剤の添加率は汚泥固形分に対しo、+
3wt%とじた場合で、オゾン処理時間を5分間、オゾ
ン濃度は2 w t%の時の測定値である。この表2に
示した結果によっても、5分間程度オゾンケ曝気して脱
水婚、液との接触火した結果、濾液の粘度は水と同程度
まで低下をするし、その濾液の目視結果では発泡現象も
発生しな力1りだ。
According to Table 1, after 5 minutes of ozone aeration, the organic polymer flocculant loses its high viscosity and exhibits a viscosity equivalent to that of water. In addition, the cation group, which is an indicator of the viscosity and physical properties of an organic polymer flocculant, was 4.5 (meq/S') before treatment in the case of Imolok IViP-175I-, but after ozone treatment Later on, it drops to 0.4 (meq/f) and loses its activity significantly.(Analysis of cation retention shows that
By colloid titration method using potassium bombinyl sulfate. ) Table 1 Table 2 Table 2 also shows the results of ozone treatment of the dewatered filtrate, which was discharged from the dewatering machine when treating the sewage sludge. The solid content in sewage sludge is 3w
t%, the addition rate of polymer flocculant is o, + to the sludge solid content.
The measured value was obtained when the ozone concentration was 3 wt%, the ozone treatment time was 5 minutes, and the ozone concentration was 2 wt%. According to the results shown in Table 2, the viscosity of the filtrate decreases to the same level as water as a result of aeration of ozone for about 5 minutes, dehydration, and contact with the liquid. It's only one force that can't be generated.

以上述べたように、有機高分子凝集剤水溶液そのものに
オゾンを供給して接触させた場合に、粘度低下が生ずる
し、有機高分子凝集剤を含イラする脱水濾液に対しても
園等に粘度が低下する久)で次の効果が得られた。
As mentioned above, when ozone is supplied and brought into contact with the organic polymer flocculant aqueous solution itself, the viscosity decreases, and the viscosity of the dehydrated filtrate containing the organic polymer flocculant also decreases. The following effects were obtained when

排水の毒性がなくなり粘性が水と同等になることから、
排水処理工程のどこへ放流しても処理の低下を招くこと
がなくなったし、河川への放流をしても発泡がないので
流水域の景観が増し1こと1司時に、風波によっての飛
散付着を防止した。更には無毒性水であるので魚貝類の
斃死や植物の生育障害等がなくなったのであZ)。
Because the toxicity of wastewater disappears and the viscosity becomes equal to that of water,
No matter where in the wastewater treatment process it is discharged, it no longer causes a deterioration in the treatment quality, and even when discharged into a river, there is no foaming, which improves the appearance of the watershed.1. was prevented. Furthermore, since the water is non-toxic, there is no risk of death of fish or shellfish or growth problems of plants.

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

第1図は本発明の一実施例を示すフローチャート図。 1:M気槽、3=ニオジン生機−5=ディフユー閉 )
口 /b /     i   −
FIG. 1 is a flowchart showing one embodiment of the present invention. 1:M air tank, 3=Niodine greige machine-5=Diffuse closed)
Mouth/b/i-

Claims (1)

【特許請求の範囲】[Claims] 有機高分子凝集剤を含有する排水の処理方法において、
排水に鉱酸を添加してPH7以下とし、オゾン濃度を1
〜5 wt%の比で排水と10分間以下の気液接触をも
ったことを特徴とする排水の処理方法。
In a method for treating wastewater containing an organic polymer flocculant,
Add mineral acid to the wastewater to lower the pH to 7 or lower, and reduce the ozone concentration to 1.
A method for treating wastewater, characterized by having gas-liquid contact with the wastewater at a ratio of ~5 wt% for 10 minutes or less.
JP6189883A 1983-04-08 1983-04-08 Treatment of waste water Pending JPS59186696A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6189883A JPS59186696A (en) 1983-04-08 1983-04-08 Treatment of waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6189883A JPS59186696A (en) 1983-04-08 1983-04-08 Treatment of waste water

Publications (1)

Publication Number Publication Date
JPS59186696A true JPS59186696A (en) 1984-10-23

Family

ID=13184418

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6189883A Pending JPS59186696A (en) 1983-04-08 1983-04-08 Treatment of waste water

Country Status (1)

Country Link
JP (1) JPS59186696A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6195500U (en) * 1984-11-29 1986-06-19
JPS61173853A (en) * 1985-01-25 1986-08-05 Matsushita Electric Ind Co Ltd Curved surface creating and grinding device
JPS61130233U (en) * 1985-01-31 1986-08-14

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6195500U (en) * 1984-11-29 1986-06-19
JPS61173853A (en) * 1985-01-25 1986-08-05 Matsushita Electric Ind Co Ltd Curved surface creating and grinding device
JPS61130233U (en) * 1985-01-31 1986-08-14

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