JPS62121688A - Method for treating oil-containing waste water - Google Patents

Method for treating oil-containing waste water

Info

Publication number
JPS62121688A
JPS62121688A JP26230485A JP26230485A JPS62121688A JP S62121688 A JPS62121688 A JP S62121688A JP 26230485 A JP26230485 A JP 26230485A JP 26230485 A JP26230485 A JP 26230485A JP S62121688 A JPS62121688 A JP S62121688A
Authority
JP
Japan
Prior art keywords
tank
oil
waste water
scum
pressure flotation
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
JP26230485A
Other languages
Japanese (ja)
Other versions
JPH0410397B2 (en
Inventor
Takashi Sei
静 孝
Yoshiji Nishimoto
西本 俶士
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.)
Kobe Steel Ltd
Shinko Pfaudler Co Ltd
Original Assignee
Kobe Steel Ltd
Shinko Pfaudler 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 Kobe Steel Ltd, Shinko Pfaudler Co Ltd filed Critical Kobe Steel Ltd
Priority to JP26230485A priority Critical patent/JPS62121688A/en
Publication of JPS62121688A publication Critical patent/JPS62121688A/en
Publication of JPH0410397B2 publication Critical patent/JPH0410397B2/ja
Granted legal-status Critical Current

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  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Physical Water Treatments (AREA)

Abstract

PURPOSE:To perfectly remove floated oil while shortening the stagnation time of said oil in an oil separation tank, by providing a process for separating the floated oil in a pressure flotation tank to which no chemicals are added to the post-stage of a process for separating the floated oil in the oil separation tank. CONSTITUTION:Oil-containing waste water is supplied to an oil separation tank 1 and sent to a pressure flotation tank 4 from a raw water tank 2 by a pump 3. The waste water is recirculated in the pressure flotation tank 4 by a water recirculation pump 5 to be mixed with air during recirculation and subsequently mixed with inflow waste water through a stagnation tank 6. The waste water is supplied to a flocculation/pressure flotation/concn. tank 9 from the pressure flotation tank 4 through a mixing tank 7 and a reaction tank 8 and recirculated in the tank 9 by a water recirculation pump 10 to be mixed with air and subsequently mixed with inflow waste water through a stagnation tank 11. By this method, the injection amount of a flocculant can be reduced and the handling of conc. scum becomes easy.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、含油廃水の処理方法に関するものであり、例
えば冷間圧延工場から発生する含油廃水の処理方法等に
好適に適用しうる含油廃水処理方法に関するものである
[Detailed Description of the Invention] [Field of Industrial Application] The present invention relates to a method for treating oil-containing wastewater, and for example, an oil-containing wastewater that can be suitably applied to a method for treating oil-containing wastewater generated from a cold rolling mill. This relates to a processing method.

C従来技術〕 冷間圧延においては、冷却、焼付防止、潤滑等のために
、ソリプル油、牛脂、パーム油、植物油等の圧延油と水
をスプレーノズルでロールに吹き付けており、その含油
廃水は、従来は第2図に示すような処理設備によって処
理されていた。
C. Prior art] In cold rolling, rolling oil such as soliple oil, tallow, palm oil, vegetable oil, etc. and water are sprayed onto the rolls using a spray nozzle for cooling, anti-seizure, lubrication, etc., and the oil-containing wastewater is , has conventionally been processed using processing equipment as shown in FIG.

第2図において、含油廃水はまず分離槽21に送られて
浮上油を分子i除去された後、第1段の加圧浮上分離装
置22に送られる。ここでは、まず急速攪拌槽23で酸
、アルカリの薬注によるPHコントロールと無機凝集剤
によるエマルジョンブレークが行われ、緩速攪拌槽24
で有機凝集剤によるフロックの粗大化が行われ、浮上分
離槽25で成長したフロックに微細な空気泡を付着させ
て浮上させ、浮上したスカムが播き寄せられてスカム槽
26に送られる。また、処理水をより清澄にするため、
上記第1段の加圧浮上分離装置22と同様の構造をなす
第2段の加圧浮上分離装置27が設けられ、同様の処理
が再度行なわれる。その後、処理水は中和槽28でPH
値を調整されて放流または再利用される。一方、スカム
槽26のスカムは、濃縮機29で水分を落として焼却し
て処分される。
In FIG. 2, oil-containing wastewater is first sent to a separation tank 21, where molecules i of floating oil are removed, and then sent to a first-stage pressurized flotation separation device 22. Here, first in the rapid stirring tank 23, pH control by acid and alkali injection and emulsion breaking using an inorganic flocculant are performed, and then in the slow stirring tank 24.
The flocs are coarsened using an organic flocculant, and the grown flocs are made to float with fine air bubbles attached to them in the flotation separation tank 25, and the floated scum is sown and sent to the scum tank 26. In addition, to make the treated water clearer,
A second-stage pressure flotation separation device 27 having the same structure as the first-stage pressure flotation separation device 22 is provided, and the same process is performed again. After that, the treated water goes to the neutralization tank 28 to
The value is adjusted and released or reused. On the other hand, the scum in the scum tank 26 is disposed of by removing moisture in a concentrator 29 and incinerating it.

ところが、このような処理方法では、分離槽21だけで
は浮上油を完全に分離することが困雛で゛ある。そのた
め、次工程の廃水中に浮上油が混入し、エマルジョンブ
レークのために多量の凝集剤が必要になるという問題が
あり、また浮上スカムに浮上油が混入するとスカムの脱
水、ハンドリングに問題を生ずることになる。
However, in such a treatment method, it is difficult to completely separate the floating oil using the separation tank 21 alone. Therefore, there is a problem that floating oil gets mixed into the wastewater of the next process, and a large amount of flocculant is required to break the emulsion.Furthermore, when floating oil gets mixed into the floating scum, it causes problems in dewatering and handling of the scum. It turns out.

また、浮上スカムは通常1〜2%で排出されるため、焼
却処理を行うためには上記のように濃縮する必要があり
、また酸分解してスカムから油を分離する場合において
も、濃縮することにより酸の添加量を少なくすることが
できる。そのための浮上スカムの濃縮法としては、■デ
カンターによる遠心分離法、■ろ布による重力脱水法、
■風乾床による天日乾燥法等があるが、上記■■の方法
は薬品の添加が必要であり、また上記■の方法は場所と
臭気の問題があり、浮上スカムの濃縮に特別な、しかも
問題のある脱水設備を必要とするという問題がある。
In addition, since floating scum is normally discharged at a concentration of 1 to 2%, it is necessary to concentrate it as described above in order to perform incineration treatment, and when separating oil from scum by acid decomposition, it is necessary to concentrate it. This allows the amount of acid added to be reduced. Methods for concentrating floating scum for this purpose include: ■ Centrifugation using a decanter, ■ Gravity dehydration using filter cloth,
■There are sun drying methods using air-drying beds, etc., but the above method ■■ requires the addition of chemicals, and the above method ■ has problems with space and odor. There is a problem in that it requires problematic dehydration equipment.

〔発明の目的〕[Purpose of the invention]

本発明は上記従来の問題点を解決するためになされたも
のであって、含油廃水から浮上油を完全に分離除去して
エマルジョンブレークのための凝集剤の添加量を少なく
することができ、かつスカムの濃縮も特別な脱水設備な
しで行える含油廃水の処理方法の提供を目的とするもの
である。
The present invention has been made to solve the above-mentioned conventional problems, and is capable of completely separating and removing floating oil from oil-containing wastewater, reducing the amount of flocculant added for emulsion breaking, and The purpose of the present invention is to provide a method for treating oil-containing wastewater that can also concentrate scum without special dehydration equipment.

〔発明の構成〕[Structure of the invention]

本発明にかかる含油廃水の処理方法は、含油廃水から油
分離槽にて浮上油を分離した後、無薬注で加圧浮上槽に
てさらに浮上油を分離して浮上油を2段階で除去し、そ
の後エマルジョンブレークし凝集剤を添加して、分離さ
れた油分を凝集加圧浮上濃縮槽にてスカムとして浮上さ
せるとともに濃縮して除去することを特徴とするもので
ある。
The method for treating oil-containing wastewater according to the present invention involves separating floating oil from oil-containing wastewater in an oil separation tank, and then further separating the floating oil in a pressurized flotation tank without using chemicals to remove the floating oil in two stages. After that, emulsion breaking is performed, a flocculant is added, and the separated oil is floated as scum in a coagulation pressurized flotation concentration tank, and is concentrated and removed.

〔実施例〕〔Example〕

以下、本発明の一実施例を第1図に基づいて説明する。 An embodiment of the present invention will be described below with reference to FIG.

まず、処理設備の概略を含油廃水の流れに沿って説明す
ると、含油廃水は油分離槽1に供給され、原水槽2から
ポンプ3にて加圧浮上槽4に送られる。この加圧浮上槽
4では廃水が循環水ポンプ5で循環され、循環中に空気
を混合された後、滞溜槽6を経て流入廃水に混合される
。廃水はこの加圧浮上槽4から混合槽7・反応槽8を介
して凝集加圧浮上濃縮槽9に供給される。この凝集加圧
浮上濃縮槽9においても、廃水は循環水ポンプ10で循
環され、循環中に空気を混合された後、滞溜槽11を介
して流入廃水に混合される。
First, the outline of the treatment equipment will be explained along the flow of oil-containing wastewater. Oil-containing wastewater is supplied to an oil separation tank 1 and sent from a raw water tank 2 to a pressurized flotation tank 4 by a pump 3. In this pressurized flotation tank 4, wastewater is circulated by a circulating water pump 5, and after being mixed with air during circulation, it is mixed with inflowing wastewater via a retention tank 6. The wastewater is supplied from this pressurized flotation tank 4 to a coagulation pressurized flotation concentration tank 9 via a mixing tank 7 and a reaction tank 8. In this coagulation pressurized flotation concentration tank 9 as well, the wastewater is circulated by the circulating water pump 10, and after being mixed with air during the circulation, it is mixed with the inflowing wastewater via the retention tank 11.

次に、上記処理設備による処理方法を説明する。Next, a processing method using the above processing equipment will be explained.

含油廃水は油分離槽1にて浮上油が分離される。Floating oil is separated from the oil-containing wastewater in an oil separation tank 1.

この分離槽1での滞溜時間は約2〜3時間程度と、従来
の12時間程度に比して飛躍的に短くすることができる
。廃水中に若干残留した浮上油は、次の加圧浮上槽4に
て無薬注で分離浮上され、浮上油とエマルジョン油とが
完全に分離される。この加圧浮上槽4においては、循環
率が20〜50%、圧力が4kg/cntg、空気量が
循環量の2〜4%程度の加圧浮上条件に設定されている
。これら油分離槽1及び加圧浮上槽4で分離除去された
浮上油は焼却される。次に、浮上油を完全に除去された
廃水に、混合槽7に入る前に約5〜20■/lの有機系
のエマルジョンブレークが注入される。
The residence time in this separation tank 1 is approximately 2 to 3 hours, which is dramatically shorter than the conventional 12 hours. The floating oil slightly remaining in the wastewater is separated and floated in the next pressurized flotation tank 4 without chemical injection, and the floating oil and emulsion oil are completely separated. In this pressurized flotation tank 4, pressurized flotation conditions are set such that the circulation rate is 20 to 50%, the pressure is 4 kg/cntg, and the amount of air is about 2 to 4% of the circulation amount. The floating oil separated and removed in the oil separation tank 1 and the pressurized flotation tank 4 is incinerated. Next, approximately 5 to 20 μ/l of organic emulsion break is injected into the wastewater from which the floating oil has been completely removed before entering the mixing tank 7.

これによって、次に混合槽7で注入する無機凝集剤の注
入量を3分の1程度にすることができる。
As a result, the amount of inorganic flocculant to be injected next in the mixing tank 7 can be reduced to about one-third.

更に、無機凝集剤の注入量が少ないと、スカムを濃縮し
た場合にAA(OH)3、Fe(OH)+等の金属水酸
化物が少なくなり、油分が濃くなるため、濃縮スカムの
取扱いが容易となり、省エネルギーともなる。混合槽7
では無機凝集剤を注入して完全にエマルジョンブレーク
する。その際、無機凝集剤のみを添加してPHを4〜6
と若干低下させることにより、エマルジョンブレーク8
機能を促進させることができる。エマルジョンブレーク
された廃水は、反応槽8においてアルカリ剤にて放流可
能なPHでかつ凝集及び油の処理に最適なPHであるP
H6,0〜7.0に調整される。エマルジョンブレーク
されて水と分離した油分は、無機凝集剤の金属水酸化物
とともにスカムを形成し、凝集加圧浮上濃縮槽9にて空
気を付着されて浮上スカムとなる。この凝集加圧浮上濃
縮槽9においては、循環率が25〜50%、圧力が4k
g/crAg、空気量が循環水の2〜4%の加圧浮上条
件で作動される。この条件においても適当な滞留時間(
2〜24HR)とスカム厚み(50〜500龍)を確保
することにより、浮上スカムは10〜30%まで濃縮さ
れる。こうして濃縮されたスカムは、そのまま焼却され
、処理水は放流される。
Furthermore, if the amount of inorganic flocculant injected is small, metal hydroxides such as AA(OH)3 and Fe(OH)+ will decrease when the scum is concentrated, and the oil content will become thicker, making it difficult to handle the concentrated scum. It becomes easier and saves energy. Mixing tank 7
Then, inject an inorganic flocculant to completely break the emulsion. At that time, add only an inorganic flocculant to adjust the pH to 4 to 6.
By slightly lowering the emulsion break 8
function can be promoted. The emulsion-broken wastewater is collected in a reaction tank 8 at a pH that can be discharged with an alkaline agent and a pH that is optimal for coagulation and oil treatment.
Adjusted to H6,0-7.0. The oil separated from water by emulsion breaking forms scum together with metal hydroxide as an inorganic flocculant, and air is attached to it in the coagulation pressurized flotation concentration tank 9 to form floating scum. In this coagulation pressurized flotation concentration tank 9, the circulation rate is 25 to 50% and the pressure is 4k.
g/crAg, and the air amount is 2 to 4% of the circulating water. Even under these conditions, an appropriate residence time (
The floating scum is concentrated to 10-30% by ensuring a sufficient scum thickness (50-500 HR) and scum thickness (50-500 HR). The scum thus concentrated is incinerated as it is, and the treated water is discharged.

〔発明の効果〕〔Effect of the invention〕

本発明の含油廃水の処理方法によれば、以上のように、
浮上油を油分離槽で分離させる工程の後段に、無薬注の
加圧浮上槽で浮上油を分離させる工程を設けていること
により、油分離槽での滞溜時間を従来に比べて格段に短
くできるとともに、浮上油を完全に除去することができ
、その結果、次工程ではエマルジョン化した油分のみを
処理すればよいことになる。これによってエマルジョン
ブレーク及び凝集剤の注入量を低減することができる。
According to the method for treating oil-containing wastewater of the present invention, as described above,
By installing a step in which floating oil is separated in a pressurized flotation tank without chemical injection after the process of separating the floating oil in an oil separation tank, the residence time in the oil separation tank is significantly reduced compared to conventional methods. In addition to being able to completely remove the floating oil, only the emulsified oil needs to be treated in the next step. This makes it possible to reduce the amount of emulsion break and coagulant injection.

また、そのためにスカムを濃縮した場合に、凝集剤によ
る金属酸化物が少なくなり油分が濃くなるため、濃縮ス
カムの取扱いが容易になるとともに、焼却時に省エネル
ギを図ることができる。
Furthermore, when the scum is concentrated for this purpose, the amount of metal oxides caused by the coagulant decreases and the oil content becomes thicker, making it easier to handle the concentrated scum and saving energy during incineration.

さらに、特別なスカムの濃縮設備と薬品を必要とせずに
スカムを濃縮できる。従って、含油廃水処理の迅速化、
設備の簡略化、薬品の節約、省エネルギー、省スペース
等の効果を奏する。
Furthermore, the scum can be concentrated without the need for special scum concentration equipment and chemicals. Therefore, speeding up oil-containing wastewater treatment,
It has the effect of simplifying equipment, saving chemicals, saving energy, and saving space.

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

第1図は本発明の一実施例のフローチャート、第2図は
従来例のフローチャートである。 1は油分離槽、4は加圧浮上槽、7は混合槽、8は反応
槽、9は凝集加圧浮上濃縮槽である。
FIG. 1 is a flowchart of an embodiment of the present invention, and FIG. 2 is a flowchart of a conventional example. 1 is an oil separation tank, 4 is a pressurized flotation tank, 7 is a mixing tank, 8 is a reaction tank, and 9 is a coagulation pressurized flotation concentration tank.

Claims (1)

【特許請求の範囲】[Claims] 1、含油廃水から油分離槽にて浮上油を分離した後、無
薬注で加圧浮上槽にてさらに浮上油を分離して浮上油を
2段階で除去し、その後エマルジョンブレークし凝集剤
を添加して、分離された油分を凝集加圧浮上濃縮槽にて
スカムとして浮上させるとともに濃縮して除去すること
を特徴とする含油廃水の処理方法。
1. After separating the floating oil from oil-containing wastewater in an oil separation tank, the floating oil is further separated in a pressurized flotation tank without chemical injection, and the floating oil is removed in two stages. After that, the emulsion is broken and a flocculant is removed. A method for treating oil-containing wastewater, which comprises adding the separated oil to the surface as scum in a coagulation and pressure flotation concentration tank, and concentrating and removing the oil.
JP26230485A 1985-11-20 1985-11-20 Method for treating oil-containing waste water Granted JPS62121688A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP26230485A JPS62121688A (en) 1985-11-20 1985-11-20 Method for treating oil-containing waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP26230485A JPS62121688A (en) 1985-11-20 1985-11-20 Method for treating oil-containing waste water

Publications (2)

Publication Number Publication Date
JPS62121688A true JPS62121688A (en) 1987-06-02
JPH0410397B2 JPH0410397B2 (en) 1992-02-25

Family

ID=17373924

Family Applications (1)

Application Number Title Priority Date Filing Date
JP26230485A Granted JPS62121688A (en) 1985-11-20 1985-11-20 Method for treating oil-containing waste water

Country Status (1)

Country Link
JP (1) JPS62121688A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102226381A (en) * 2011-05-05 2011-10-26 威海怡和专用设备制造股份有限公司 Method for treating abandoned drilling fluid of oilfield
CN102992558A (en) * 2012-11-26 2013-03-27 司军 Method and system for capturing and masking heavy metal in well drilling wastes
JP2016507370A (en) * 2013-01-16 2016-03-10 ドン ベ,ヒ Processing equipment and processing method using waste water and palm by-product finally discharged from palm oil production processing
JP2016120452A (en) * 2014-12-24 2016-07-07 栗田工業株式会社 Method of reducing viscosity of oil-containing scum

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6350025B2 (en) * 2014-06-26 2018-07-04 栗田工業株式会社 Oil-water separation method and oil-water separation agent for oil-containing scum or oil-containing wastewater

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102226381A (en) * 2011-05-05 2011-10-26 威海怡和专用设备制造股份有限公司 Method for treating abandoned drilling fluid of oilfield
CN102992558A (en) * 2012-11-26 2013-03-27 司军 Method and system for capturing and masking heavy metal in well drilling wastes
JP2016507370A (en) * 2013-01-16 2016-03-10 ドン ベ,ヒ Processing equipment and processing method using waste water and palm by-product finally discharged from palm oil production processing
JP2016120452A (en) * 2014-12-24 2016-07-07 栗田工業株式会社 Method of reducing viscosity of oil-containing scum

Also Published As

Publication number Publication date
JPH0410397B2 (en) 1992-02-25

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