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JPS6034792A - Treatment of waste water containing oil - Google Patents

Treatment of waste water containing oil

Info

Publication number
JPS6034792A
JPS6034792A JP14357183A JP14357183A JPS6034792A JP S6034792 A JPS6034792 A JP S6034792A JP 14357183 A JP14357183 A JP 14357183A JP 14357183 A JP14357183 A JP 14357183A JP S6034792 A JPS6034792 A JP S6034792A
Authority
JP
Japan
Prior art keywords
water
waste water
wastewater
oil
oxidation
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
JP14357183A
Other languages
Japanese (ja)
Other versions
JPH0117433B2 (en
Inventor
Yukio Okuyama
奥山 幸男
Tadashi Yamazaki
山崎 征
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 Ltd
Original Assignee
Hitachi Plant Construction Co Ltd
Hitachi Plant Engineering and Construction 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 Hitachi Plant Construction Co Ltd, Hitachi Plant Engineering and Construction Co Ltd filed Critical Hitachi Plant Construction Co Ltd
Priority to JP14357183A priority Critical patent/JPS6034792A/en
Publication of JPS6034792A publication Critical patent/JPS6034792A/en
Publication of JPH0117433B2 publication Critical patent/JPH0117433B2/ja
Granted legal-status Critical Current

Links

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  • Separation Using Semi-Permeable Membranes (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PURPOSE:To obtain easily waste water having quality permissible with respect to standard for final effluent by oxidizing waste water contg. oil and emulsifier with H2O2 and ferrous sulphate at pH3-5, performing then flocculation and settling at pH6-8 to separate solid from liquid. CONSTITUTION:H2O2 and ferrous sulphate are added to concentrated waste water or permeated water obtd. by ultrafiltration of concentrated waste water to perform oxidation by adding if necessary mineral acid or alkali and maintaining at pH3-5. The pH of oxidized water is adjusted to 6-8 with alkali, and oxidation product and hydroxide of iron, etc. are settled by flocculation by adding flocculant. In this stage, waste water produced by washing may be mixed with the oxidation treated water and flocculated together. Since, emulsions are destructed sufficiently by oxidation in this process, the flocculation is performed effectively, and deposited flocculated solid can be subjected to solid/liquid separation by the conventional process.

Description

【発明の詳細な説明】 本発明は、油含有廃水の処理方法に関する。[Detailed description of the invention] The present invention relates to a method for treating oil-containing wastewater.

自動車、機械加工、金属加工等の工場では各種の油が使
用され、特に切削加工時には切削油が使用され、これら
の油とその油分を乳化分散する乳化剤を含む廃水が排出
される。このような油含有廃水(以下、濃厚廃水と記す
)は、大きい汚濁負荷を示し、ヘキサン抽出物質、BO
D、、CODがいずれも致方mg/I!、に達する場合
があり、著しし、1汚濁源となっている。また、前記の
ような工場では、洗浄剤を含む洗浄廃水も排出され、こ
の洗浄廃水の汚濁負荷も大きい。
Various types of oil are used in automobile, machining, and metal processing factories, and cutting oil is especially used during cutting processes, and wastewater containing these oils and emulsifiers that emulsify and disperse the oil components is discharged. Such oil-containing wastewater (hereinafter referred to as concentrated wastewater) exhibits a large pollution load and contains hexane extractables, BO
D,, COD are all wrong mg/I! , and is a significant source of pollution. Further, in the above-mentioned factories, cleaning wastewater containing cleaning agents is also discharged, and the pollution load of this cleaning wastewater is large.

従来、この種の廃水を処理する場合、濃厚廃水又は濃厚
廃水と洗浄廃水との混合液に鉱酸を加えてpH1〜3と
し、油のエマルジョンを破壊し、油分を浮上分離した後
、凝集沈澱処理、微生物酸化処理、’rf過、活性炭吸
着処理等を適宜組み合わせ変化すると、エマルシロンの
破壊が充分に行われず、後段の処理に致命的な障害を引
き起こすことがしばしばあり、処理の安定性に欠け、放
流基準水質を達成できない場合すらあった。
Conventionally, when treating this kind of wastewater, mineral acid is added to concentrated wastewater or a mixture of concentrated wastewater and washing wastewater to adjust the pH to 1 to 3, the oil emulsion is broken, the oil is floated and separated, and then coagulated and precipitated. If appropriate combinations of treatment, microbial oxidation treatment, 'RF filtration, activated carbon adsorption treatment, etc. are used, Emulsilon will not be destroyed sufficiently, which will often cause fatal problems in subsequent treatments, resulting in a lack of processing stability. There were even cases where the discharge water quality standards could not be achieved.

本発明の目的は、前記の従来技術の欠点を解消し、安定
確実に処理可能で、かつ容易に放流基準水質が得られる
油含有廃水の処理方法を提供することにある。この目的
は、本発明によれば、油のエマルシコンを酸化分解によ
り破壊することによって達成される。
An object of the present invention is to provide a method for treating oil-containing wastewater that eliminates the drawbacks of the prior art described above, that can be treated stably and reliably, and that can easily meet the standard discharge water quality. This objective is achieved according to the invention by destroying the emulsicone of the oil by oxidative decomposition.

本発明方法は、廃水をpH3〜5で過酸化水素及び硫酸
第一鉄により酸化処理し、酸化処理水をpH6〜8で凝
集性根処理し、固液分離することを特徴とする。
The method of the present invention is characterized in that wastewater is oxidized with hydrogen peroxide and ferrous sulfate at a pH of 3 to 5, and the oxidized water is subjected to cohesive root treatment at a pH of 6 to 8, followed by solid-liquid separation.

過酸化水素及び硫酸第一鉄は強力な酸化剤であり、フェ
ントン試薬として知られているが、これを油含有廃水の
処理に使用することは知られていなかった。本発明によ
り、この酸化剤を濃厚廃水に添加すると、濃厚廃水中の
乳化剤の大部分は、その種類、即ち乳化力の差異によら
ず酸化分解され、エマルジョンが破壊されるとともに、
油分が除去される。
Although hydrogen peroxide and ferrous sulfate are strong oxidizing agents and are known as Fenton's reagents, their use in treating oil-containing wastewater has not been known. According to the present invention, when this oxidizing agent is added to concentrated wastewater, most of the emulsifier in the concentrated wastewater is oxidized and decomposed regardless of the type of emulsifying agent, that is, the difference in emulsifying power, and the emulsion is destroyed.
Oil is removed.

本発明方法において、予め限外8r過装置によって透過
処理し、濃厚廃水中の油分の大部分を除去し、次いで透
過水中に漏出する乳化剤を本発明方法により分解除去し
てもよい。
In the method of the present invention, most of the oil in the concentrated wastewater may be removed by permeation treatment using an ultra-8R filtration device in advance, and then the emulsifier leaking into the permeated water may be decomposed and removed by the method of the present invention.

濃厚廃水又は濃厚廃水を限外シ戸遇した透過水に過酸化
水素及び硫酸第一鉄を添加し、必要に応じて#L酸又は
アルカリを加えてpl(3〜5に保持し、酸化処理する
Hydrogen peroxide and ferrous sulfate are added to the concentrated wastewater or the permeated water obtained by treating the concentrated wastewater in an ultracentrifugal manner, and if necessary, #L acid or alkali is added to maintain the PL (3 to 5), followed by oxidation treatment. do.

酸化処理水を次に、ア゛ルカリを用いてp)16〜8に
調整し、凝集剤を添加して酸化生成物や鉄の水酸化物等
を析出凝集させる。その際、酸化処理水に洗浄廃水を混
合して一緒に凝集処理してもよい。
Next, the oxidized water is adjusted to p) 16 to 8 using alkali, and a flocculant is added to precipitate and flocculate oxidation products, iron hydroxide, and the like. At this time, washing waste water may be mixed with the oxidized water and coagulated together.

本発明方法によれば、前記の酸化処理によりエマルジョ
ンが充分に破壊されているので、凝集処理は効率よく行
われる。析出、凝集させた固形物は常法で固液分離する
ことができる。
According to the method of the present invention, since the emulsion is sufficiently destroyed by the oxidation treatment, the aggregation treatment can be carried out efficiently. The precipitated and aggregated solids can be separated into solid and liquid by a conventional method.

前記の処理により、廃水中のへキサン抽出物質、BOD
及びCODで表示される有機汚濁物を極めて効率よく除
去することができる。こうして得た処理水は、放流基準
水質に達しており、そのまま放流することができるが、
更に高度な水質を望むを安定確実に処理することができ
、容易に放流基準水質を達成することができる。
Through the above treatment, hexane extractables, BOD
Organic pollutants indicated by COD and COD can be removed very efficiently. The treated water obtained in this way has reached the discharge standard water quality and can be discharged as is.
Even higher quality water can be treated stably and reliably, and discharge standard water quality can be easily achieved.

次に、実施例に基づいて本発明を詳述するが、本発明は
これに限定されるものではない。なお、実施例に使用す
る廃水は、自動車製造工場から排出された濃厚な切削油
を含む濃厚廃水及び洗浄廃水であり、下記の第1表に示
す水質を有する。
Next, the present invention will be described in detail based on Examples, but the present invention is not limited thereto. The wastewater used in the examples is concentrated wastewater containing concentrated cutting oil and washing wastewater discharged from an automobile manufacturing factory, and has the water quality shown in Table 1 below.

第1表 実施例1 第1表に示した水質の濃厚廃水を採取し、該廃水11に
過酸化水素5000■/l及び硫酸第一鉄11000■
/lを添加した後、pnaに調節して酸化処理した。こ
の酸化処理水を第1表に示した洗浄廃水と混合した後、
苛性ソーダを添加してpHを6〜8に調整し、高分子凝
集剤を添加して凝集させ、静置し、上澄水をNa 5 
A i戸紙を用いて1r過し、該1濾過水の水質を測定
し、結果を下記の第2表に処理水入として示す。
Table 1 Example 1 Concentrated wastewater with the water quality shown in Table 1 was collected, and the wastewater 11 was mixed with 5000 μ/l of hydrogen peroxide and 11000 μl of ferrous sulfate.
After adding /l, it was adjusted to pna and oxidized. After mixing this oxidized water with the cleaning wastewater shown in Table 1,
Add caustic soda to adjust the pH to 6 to 8, add a polymer flocculant to flocculate, leave to stand, and convert the supernatant water to Na 5
The water was filtered for 1 hour using Ai paper, and the quality of the filtrated water was measured, and the results are shown in Table 2 below as treated water.

この処理水Aに粉末活性炭25000■/lを添加し、
15時間振盪した後、No5Cir紙でシ濾過し、)r
″過水水質を測定し、同様に結果を下記の第2表に処理
水Bとして示す。
25,000 μ/l of powdered activated carbon was added to this treated water A,
After shaking for 15 hours, it was filtered with No5Cir paper,
``The quality of the treated water was measured, and the results are similarly shown in Table 2 below as treated water B.

第2表 第2表から判るように、本発明方法によれば、高濃度の
有機汚染物質を含有する廃水を極めて容易に浄化するこ
とができ、放流基準水質内の水質にすることができた。
As can be seen from Table 2, according to the method of the present invention, wastewater containing high concentrations of organic pollutants could be purified extremely easily, and the water quality could be brought to within the effluent standard water quality. .

実施例2 第1表に示した水質の濃厚廃水をポリオレフィン系膜を
使用した限外−過装置で、圧力1.7kg/d、流速1
.5m/秒で一過し、透過水llに過酸化水素3000
■/j2及び硫酸第一鉄5400■/lを添加し、pH
を3に調整して酸化処理した。
Example 2 Concentrated wastewater with the water quality shown in Table 1 was processed using an ultrafiltration device using a polyolefin membrane at a pressure of 1.7 kg/d and a flow rate of 1.
.. Passed at 5 m/sec, and added 3000 ml of hydrogen peroxide to 1 liter of permeated water.
■/j2 and 5400 ■/l of ferrous sulfate were added, and the pH
was adjusted to 3 and oxidized.

該酸化処理水を洗浄廃水と混合し、苛性ソーダでpHを
6〜8に調整し、次いで高分子凝集剤を添加して凝集処
理し、静置し、上澄水をNo、 5 A ’tP紙で一
過し、2r過水の水質を測定し、結果を第3表に処理水
Cとして示す。
The oxidized water was mixed with washing waste water, the pH was adjusted to 6 to 8 with caustic soda, then a polymer flocculant was added for flocculation treatment, left to stand, and the supernatant water was washed with No. 5 A'tP paper. The water quality of the 2R perfused water was measured, and the results are shown in Table 3 as treated water C.

処理水Cに粉末活性炭25000■/βを添加し、15
時間振盪した後、h3.5 C’r戸紙で1濾過し、r
過水の水質を測定し、結果を第3表に処理水りとして示
す。
Powdered activated carbon 25,000 μ/β was added to treated water C, and 15
After shaking for an hour, filter through 3.5 C'r paper, and
The quality of the treated water was measured and the results are shown in Table 3 as treated water.

第3表 第3表から判るように、限外−過により乳化対を除いて
大部分の有機汚濁物質を除去することができ、残留する
乳化剤は過酸化水素及び第一鉄イオンによって極めて良
好に分解除去され、更に活性炭吸着処理水は極めて良好
な水質であった。
Table 3 As can be seen from Table 3, ultrafiltration can remove most of the organic pollutants except for emulsifiers, and the remaining emulsifiers are very well treated by hydrogen peroxide and ferrous ions. The activated carbon adsorption treated water was of extremely good quality.

特許出願人 日立プラント建設株式会社patent applicant Hitachi Plant Construction Co., Ltd.

Claims (3)

【特許請求の範囲】[Claims] (1)油とこの油分を乳化分散させる乳化剤とを含有す
る廃水を浄化するため、廃水をpH3〜5で過酸化水素
及び硫酸第一鉄により酸化処理し、酸化処理水をpl+
6〜8で凝集沈澱処理し、固液分離することを特徴とす
る油含有廃水の処理方法。
(1) In order to purify wastewater containing oil and an emulsifier that emulsifies and disperses the oil, the wastewater is oxidized with hydrogen peroxide and ferrous sulfate at pH 3 to 5, and the oxidized water is pl+
A method for treating oil-containing wastewater, which comprises performing coagulation-sedimentation treatment and solid-liquid separation in steps 6 to 8.
(2)廃水が切削油を含む廃水である特許請求の範囲第
1項記載の方法。
(2) The method according to claim 1, wherein the wastewater is wastewater containing cutting oil.
(3)廃水を予め限外−過した後、酸化処理する特許請
求の範囲第1項記載の方法。
(3) The method according to claim 1, wherein the wastewater is subjected to ultrafiltration in advance and then subjected to oxidation treatment.
JP14357183A 1983-08-05 1983-08-05 Treatment of waste water containing oil Granted JPS6034792A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14357183A JPS6034792A (en) 1983-08-05 1983-08-05 Treatment of waste water containing oil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14357183A JPS6034792A (en) 1983-08-05 1983-08-05 Treatment of waste water containing oil

Publications (2)

Publication Number Publication Date
JPS6034792A true JPS6034792A (en) 1985-02-22
JPH0117433B2 JPH0117433B2 (en) 1989-03-30

Family

ID=15341841

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14357183A Granted JPS6034792A (en) 1983-08-05 1983-08-05 Treatment of waste water containing oil

Country Status (1)

Country Link
JP (1) JPS6034792A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5472619A (en) * 1993-09-03 1995-12-05 Birko Corporation Waste water treatment with peracetic acid compositions
US5647997A (en) * 1993-09-03 1997-07-15 Birko Corporation Waste water treatment with peracid compositions
EP1157972A1 (en) * 2000-05-26 2001-11-28 Apostolos Vlissidis A method of processing oil-plant wastes
EP1714945A1 (en) * 2005-04-18 2006-10-25 Chemie X 2000 Schrupstock Gmbh & Co. Kg Method for processing the liquid wastes of oil extracting plant
JP2009028616A (en) * 2007-07-26 2009-02-12 Daicen Membrane Systems Ltd Wastewater treatment method
CN103663793A (en) * 2013-12-12 2014-03-26 中国航空规划建设发展有限公司 High-concentration emulsified liquid wastewater treatment method
JP2014159018A (en) * 2013-02-20 2014-09-04 Mitsubishi Rayon Co Ltd Flocculation method of oil inclusion cleaning waste water
CN112079494A (en) * 2020-06-14 2020-12-15 太原理工大学 Method for treating emulsion wastewater

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5472619A (en) * 1993-09-03 1995-12-05 Birko Corporation Waste water treatment with peracetic acid compositions
US5647997A (en) * 1993-09-03 1997-07-15 Birko Corporation Waste water treatment with peracid compositions
EP1157972A1 (en) * 2000-05-26 2001-11-28 Apostolos Vlissidis A method of processing oil-plant wastes
EP1714945A1 (en) * 2005-04-18 2006-10-25 Chemie X 2000 Schrupstock Gmbh & Co. Kg Method for processing the liquid wastes of oil extracting plant
JP2009028616A (en) * 2007-07-26 2009-02-12 Daicen Membrane Systems Ltd Wastewater treatment method
JP2014159018A (en) * 2013-02-20 2014-09-04 Mitsubishi Rayon Co Ltd Flocculation method of oil inclusion cleaning waste water
CN103663793A (en) * 2013-12-12 2014-03-26 中国航空规划建设发展有限公司 High-concentration emulsified liquid wastewater treatment method
CN112079494A (en) * 2020-06-14 2020-12-15 太原理工大学 Method for treating emulsion wastewater
CN112079494B (en) * 2020-06-14 2022-06-17 太原理工大学 Method for treating emulsion wastewater

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Publication number Publication date
JPH0117433B2 (en) 1989-03-30

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