JPH0117433B2 - - Google Patents
Info
- Publication number
- JPH0117433B2 JPH0117433B2 JP14357183A JP14357183A JPH0117433B2 JP H0117433 B2 JPH0117433 B2 JP H0117433B2 JP 14357183 A JP14357183 A JP 14357183A JP 14357183 A JP14357183 A JP 14357183A JP H0117433 B2 JPH0117433 B2 JP H0117433B2
- Authority
- JP
- Japan
- Prior art keywords
- wastewater
- oil
- water
- oxidized
- treatment
- 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.)
- Expired
Links
- 239000002351 wastewater Substances 0.000 claims description 36
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 32
- 239000003921 oil Substances 0.000 claims description 17
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 14
- 238000000034 method Methods 0.000 claims description 11
- 239000003995 emulsifying agent Substances 0.000 claims description 7
- 239000011790 ferrous sulphate Substances 0.000 claims description 6
- 235000003891 ferrous sulphate Nutrition 0.000 claims description 6
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 claims description 6
- 229910000359 iron(II) sulfate Inorganic materials 0.000 claims description 6
- 230000003647 oxidation Effects 0.000 claims description 6
- 238000007254 oxidation reaction Methods 0.000 claims description 6
- 238000000108 ultra-filtration Methods 0.000 claims description 4
- 239000010730 cutting oil Substances 0.000 claims description 3
- 239000007788 liquid Substances 0.000 claims description 3
- 230000001804 emulsifying effect Effects 0.000 claims description 2
- 238000000926 separation method Methods 0.000 claims description 2
- 238000004062 sedimentation Methods 0.000 claims 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 10
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 239000000839 emulsion Substances 0.000 description 6
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 description 6
- 238000005406 washing Methods 0.000 description 5
- 239000002957 persistent organic pollutant Substances 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 239000006228 supernatant Substances 0.000 description 3
- 239000002253 acid Substances 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 239000012632 extractable Substances 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 1
- 239000012028 Fenton's reagent Substances 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 238000004220 aggregation Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- -1 and if necessary Substances 0.000 description 1
- 239000012459 cleaning agent Substances 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000005520 cutting process Methods 0.000 description 1
- 229910001448 ferrous ion Inorganic materials 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- MGZTXXNFBIUONY-UHFFFAOYSA-N hydrogen peroxide;iron(2+);sulfuric acid Chemical compound [Fe+2].OO.OS(O)(=O)=O MGZTXXNFBIUONY-UHFFFAOYSA-N 0.000 description 1
- 235000014413 iron hydroxide Nutrition 0.000 description 1
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 description 1
- 238000003754 machining Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000006864 oxidative decomposition reaction Methods 0.000 description 1
- 229920000098 polyolefin Polymers 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Landscapes
- Separation Using Semi-Permeable Membranes (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Description
本発明は、油含有廃水の処理方法に関する。
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、BOD、CODがい
ずれも数万mg/に達する場合があり、著しい汚
濁源となつている。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。
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、油のエマルジヨンを破壊し、油
分を浮上分離した後、凝集沈澱処理、微生物酸化
処理、過、活性炭吸着処理等を適宜組み合わせ
て処理を行い、放流可能な水質にしている。しか
し、このような処理方法では含まれる油又は乳化
剤の種類が変化すると、エマルジヨンの破壊が充
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つ
た。
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
エマルジヨンを酸化分解により破壊することによ
つて達成される。
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PH
6〜8で凝集沈澱処理し、固液分離することを特
徴とする。
過酸化水素及び硫酸第一鉄は強力な酸化剤であ
り、フエ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
なかつた。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、エマルジヨンが破壊されるとともに、油分が
除去される。
本発明方法において、予め限外過装置によつ
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。
濃厚廃水又は濃厚廃水を限外過した透過水に
過酸化水素及び硫酸第一鉄を添加し、必要に応じ
て鉱酸又はアルカリを加えてPH3〜5に保持し、
酸化処理する。
酸化処理水を次に、アルカリを用いてPH6〜8
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。本発明方法によれば、前記の酸化処理により
エマルジヨ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。
前記の処理により、廃水中のヘキサン抽出物
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
む場合には、更に活性炭等の吸着剤を用いて吸着
処理する。
このように、本発明方法によれば、油含有廃水
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。
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。
The present invention relates to a method for treating oil-containing wastewater. 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 hexane extractable substances, BOD, and COD can all reach tens of thousands of mg/ml, making it 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. 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 destroyed, the oil is floated and separated, and then coagulated and precipitated. Water treatment is carried out using appropriate combinations of treatment, microbial oxidation treatment, filtration, activated carbon adsorption treatment, etc., to make the water quality suitable for discharge. However, in such processing methods, if the type of oil or emulsifier contained changes, the emulsion cannot be broken sufficiently, which often causes fatal problems in subsequent processing, and the processing lacks stability. There were even cases in which the discharge standard water quality could not be achieved. 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 oil emulsion by oxidative decomposition. In the method of the present invention, wastewater is oxidized with hydrogen peroxide and ferrous sulfate at a pH of 3 to 5, and the oxidized water is
It is characterized by coagulation and precipitation treatment in steps 6 to 8, followed by solid-liquid separation. Hydrogen peroxide and ferrous sulfate are strong oxidizing agents, known as Fenton's reagent, but their use in treating oil-containing wastewater has not been known. According to the present invention, when this oxidizing agent is added to the concentrated wastewater, most of the emulsifier in the concentrated wastewater is
The emulsion is oxidized and decomposed regardless of its type, that is, its emulsifying power, and the emulsion is destroyed and the oil is removed. In the method of the present invention, most of the oil in the concentrated wastewater may be removed by permeation treatment using an ultrafiltration device in advance, and then the emulsifier leaking into the permeated water may be decomposed and removed by the method of the present invention. Hydrogen peroxide and ferrous sulfate are added to concentrated wastewater or permeated water obtained by ultrafiltering concentrated wastewater, and if necessary, mineral acid or alkali is added to maintain the pH at 3 to 5.
Oxidize. The oxidized water is then adjusted to pH 6-8 using alkali.
and add a flocculant to precipitate and flocculate oxidation products, iron hydroxide, etc. At this time, washing waste water may be mixed with the oxidized water and coagulated together. 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. By the above treatment, organic pollutants expressed as hexane extractables, BOD and COD in wastewater can be removed very efficiently. The treated water thus obtained has reached the discharge standard water quality and can be discharged as is, but if a higher quality water quality is desired, it is further subjected to adsorption treatment using an adsorbent such as activated carbon. As described above, according to the method of the present invention, oil-containing wastewater can be treated stably and reliably, and discharge standard water quality can be easily achieved. Next, the present invention will be explained in detail based on examples.
The present invention is not limited to this. In addition,
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.
【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1に過酸化水素5000mg/及び硫酸第一鉄
11000mg/を添加した後、PH3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No.5A紙を用いて過し、
該過水の水質を測定し、結果を下記の第2表に
処理水Aとして示す。
この処理水Aに粉末活性炭25000mg/を添加
し、15時間振盪した後、No.5C紙で過し、
過水の水質を測定し、同様に結果を下記の第2表
に処理水Bとして示す。[Table] Example 1 Collect concentrated wastewater with the water quality shown in Table 1, and add 5000 mg of hydrogen peroxide and ferrous sulfate to the wastewater 1.
After adding 11,000 mg/ml, the pH was adjusted to 3 and oxidation treatment was performed. After mixing this oxidized water with the washing wastewater shown in Table 1, caustic soda was added to bring the pH to 6.
~8, add a polymer flocculant to flocculate, leave to stand, filter the supernatant water using No. 5A paper,
The quality of the perfused water was measured and the results are shown in Table 2 below as treated water A. 25,000 mg of powdered activated carbon was added to this treated water A, and after shaking for 15 hours, it was filtered through No. 5C paper.
The quality of the treated water was measured, and the results are similarly shown in Table 2 below as treated water B.
【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。
実施例 2
第1表に示した水質の濃厚廃水をポリオレフイ
ン系膜を使用した限外過装置で、圧力1.7Kg/
cm2、流速1.5m/秒で過し、透過水1に過酸
化水素3000mg/及び硫酸第一鉄5400mg/を添
加し、PHを3に調整して酸化処理した。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.5A紙で過し、
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。
処理水Cに粉末活性炭25000mg/を添加し、
15時間振盪した後、No.5C紙で過し、過水
の水質を測定し、結果を第3表に処理水Dとして
示す。[Table] As can be seen from Table 2, according to the method of the present invention,
It was possible to purify wastewater containing high concentrations of organic pollutants very easily and bring the water quality within the effluent standard. 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/kg.
cm 2 at a flow rate of 1.5 m/sec, 3000 mg of hydrogen peroxide and 5400 mg of ferrous sulfate were added to the permeated water 1, and the pH was adjusted to 3 for oxidation treatment. Mix the oxidized water with washing wastewater and adjust the pH to 6~6 with caustic soda.
8, then add a polymer flocculant to flocculate, leave to stand, and filter the supernatant water through No. 5A paper.
The quality of the overwater was measured and the results are shown in Table 3.
Shown as Add 25,000 mg of powdered activated carbon to treated water C,
After shaking for 15 hours, it was filtered through No. 5C paper and the quality of the supernatant water was measured, and the results are shown in Table 3 as treated water D.
【表】
第3表から判るように、限外過により乳化剤
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
オンによつ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つた。[Table] As can be seen from Table 3, most of the organic pollutants except for the emulsifier can be removed by ultrafiltration, and the remaining emulsifier is very well treated by hydrogen peroxide and ferrous ions. The activated carbon adsorption treated water was of extremely good quality.
Claims (1)
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PH6〜8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。 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。 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。[Claims] 1. In order to purify wastewater containing oil and an emulsifier for emulsifying and dispersing the oil, the wastewater is oxidized with hydrogen peroxide and ferrous sulfate at a pH of 3 to 5, and the oxidized water is oxidized to a pH of 6. 8. A method for treating oil-containing wastewater, which comprises performing a coagulation-sedimentation treatment and solid-liquid separation. 2. The method according to claim 1, wherein the wastewater is wastewater containing cutting oil. 3. The method according to claim 1, wherein the wastewater is subjected to ultrafiltration in advance and then subjected to oxidation treatment.
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 JPS6034792A (en) | 1985-02-22 |
JPH0117433B2 true 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) |
Families Citing this family (8)
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 |
GR1003914B (en) * | 2000-05-26 | 2002-06-25 | Αποστολος Βλησιδης | A method of processing oil-plant wastes and resulting organo-humic product |
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 |
JP4781325B2 (en) * | 2007-07-26 | 2011-09-28 | ダイセン・メンブレン・システムズ株式会社 | Wastewater treatment method |
JP6134940B2 (en) * | 2013-02-20 | 2017-05-31 | 三菱ケミカル株式会社 | Coagulation treatment method for oil-containing cleaning wastewater |
CN103663793B (en) * | 2013-12-12 | 2014-12-17 | 中国航空规划建设发展有限公司 | High-concentration emulsified liquid wastewater treatment method |
CN112079494B (en) * | 2020-06-14 | 2022-06-17 | 太原理工大学 | Method for treating emulsion wastewater |
-
1983
- 1983-08-05 JP JP14357183A patent/JPS6034792A/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPS6034792A (en) | 1985-02-22 |
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