JPS58109189A - Treatment for waste water of emulsified oil - Google Patents
Treatment for waste water of emulsified oilInfo
- Publication number
- JPS58109189A JPS58109189A JP20770081A JP20770081A JPS58109189A JP S58109189 A JPS58109189 A JP S58109189A JP 20770081 A JP20770081 A JP 20770081A JP 20770081 A JP20770081 A JP 20770081A JP S58109189 A JPS58109189 A JP S58109189A
- Authority
- JP
- Japan
- Prior art keywords
- polyaluminum chloride
- oil
- emulsified oil
- added
- filtrate
- 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
Links
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Description
【発明の詳細な説明】 本発明は、乳化油廃水の処理方法に関するものである。[Detailed description of the invention] The present invention relates to a method for treating emulsified oil wastewater.
溶液中に界面活性剤などの安定剤を含み、油の微粒子が
安定化している乳化油廃水の処理方法として、従来一般
的には、Ca系薬剤の添加、あるいは電場を与えて油滴
の捧っている電荷を中和することが行なわれている。Conventional methods for treating emulsified oil wastewater, in which the solution contains stabilizers such as surfactants and stabilizes fine oil particles, include the addition of Ca-based chemicals or the application of an electric field to create oil droplets. The current charge is neutralized.
しかし、上述の如く乳化を破壊し、廃水中の油分を除去
することができても、なお廃水中には界面活性剤その他
の可溶性有機物が残存しているため、次の段階の処理と
して、活性炭吸着法、光酸化法、生物処理法などが通常
行なわれており、処理として非常に複雑である。However, even if the emulsification can be destroyed and the oil content in the wastewater can be removed as described above, surfactants and other soluble organic substances still remain in the wastewater, so activated carbon is used as the next step of treatment. Adsorption methods, photo-oxidation methods, biological treatment methods, etc. are commonly used, and the treatments are extremely complex.
本発明は、従来非常に複雑であった乳化油廃水の処理を
、比較的簡単に行なえるようにしたものであって、それ
に関し以下に説明する。The present invention makes it possible to relatively easily treat emulsified oil wastewater, which has conventionally been very complicated, and will be described below.
溶液中に界面活性剤などの安定剤を含み、油の微粒子が
安定している乳化油廃水は、−例として第1表に示す如
く、COD濃度および油分濃度が高いため、そのまま排
水することができない。Emulsified oil wastewater, which contains stabilizers such as surfactants in the solution and has stable oil particles, has a high COD concentration and oil concentration, as shown in Table 1, so it cannot be discharged as is. Can not.
そこで、上記第1表に示す如き乳化油廃水中に、無機高
分子凝集剤であるポリ塩化アルミニウム(At203に
換算して約10W/V%、以下PACという)の過剰量
を添加する。Therefore, an excess amount of polyaluminum chloride (approximately 10 W/V% in terms of At203, hereinafter referred to as PAC), which is an inorganic polymer flocculant, is added to the emulsified oil wastewater as shown in Table 1 above.
なお、PACの添加量は、乳化油廃水中の油分濃度によ
って異なるが、後述する実験例に基づく第2図の関係式
1により求められる。The amount of PAC added varies depending on the oil concentration in the emulsified oil wastewater, but is determined by the relational expression 1 in FIG. 2 based on the experimental example described later.
また、過剰量とは、乳化油廃水のPH値が4.2以下で
は、PACがそれ以上沈殿せずに可溶性のAt3+にな
るまでの量である。Moreover, the excessive amount is an amount that, when the pH value of the emulsified oil wastewater is 4.2 or less, does not cause PAC to precipitate any more and becomes soluble At3+.
さらに、凝集剤としてPACを使用した理由は、PAC
は、上、下水道をはじめ、各種の産業廃水に対し、高い
凝集力および壓、毒性を有し、かつ有機高分子凝集剤に
比較して安価なためである。Furthermore, the reason for using PAC as a flocculant is that PAC
This is because they have high cohesive strength and toxicity for various industrial wastewaters, including water and sewerage systems, and are cheaper than organic polymer flocculants.
前記の如く、乳化油廃水中に添加した過剰量のPACは
、乳化油廃水自体のPH値によってAt(OH)3を生
成し、この生成されたAt (OH)aにより大部分の
油分を凝集沈殿させ、この凝集沈殿物を濾過によって除
去する。As mentioned above, the excessive amount of PAC added to the emulsified oil wastewater generates At(OH)3 depending on the PH value of the emulsified oil wastewater itself, and the generated At(OH)a coagulates most of the oil. The flocculated precipitate is removed by filtration.
前記凝集沈殿物が除去された濾過液は、PACを前記の
如く過剰に添加したために、そのPH値が低くなってい
る(PH4,2)。The filtrate from which the coagulated precipitate was removed has a low pH value (PH 4, 2) due to the excessive addition of PAC as described above.
このPH値が低くなっている濾過液中に、後述する実験
例に基づく第3図の関係式2によって求められる量のN
a0H(10W/V%)を添加して、濾過液OPH値を
5〜7に戻し、それにより濾過液中に可溶性のAt3+
とじて存在していたPACをAt (OH)3となし、
濾過液中に残存する油分、界面活性剤などをAt(OH
)3と共に凝集沈殿させ、この凝集沈殿物を濾過によっ
て除去することにより、その濾過液中の油分濃度を11
0PP以下にすることができるのである。In this filtrate with a low pH value, the amount of N determined by the relational expression 2 in Fig. 3 based on the experimental example described later.
a0H (10 W/V%) was added to bring the filtrate OPH value back to 5-7, thereby reducing the soluble At3+ in the filtrate.
The existing PAC was converted into At(OH)3,
At(OH) removes oil, surfactant, etc. remaining in the filtrate.
)3, and by removing this coagulated precipitate by filtration, the oil concentration in the filtrate was reduced to 11.
It is possible to reduce the power to 0PP or less.
なお、中和剤としては、アンモニア、炭酸ソーダーなど
があるが、アンモニアはAt3+と錯塩を形成すること
、また炭酸ソーダーは酸性側において炭酸ガスを発生す
ることなどの問題があるため、これ等の問題がなく、シ
かも安価であるNaOHを使用した。Note that neutralizing agents include ammonia, sodium carbonate, etc., but ammonia forms a complex with At3+, and sodium carbonate generates carbon dioxide gas on the acidic side. NaOH was used because it is safe and inexpensive.
実験例
第1表に示す試料A−3を300mtビーカーに採取し
、撹拌しながら、A L 203に換算して約10W/
v%の濃度のPACをL9mt添加し、さらに充分に撹
拌した後、静置し、その溶液のもつPH値によって生成
されだAt (OH)3により、試料中の油分を凝集さ
せる。Experimental Example Sample A-3 shown in Table 1 was collected in a 300 mt beaker, and while stirring, the power was approximately 10 W/ in terms of A L 203.
After adding 9 mt of PAC having a concentration of v % and stirring thoroughly, the solution is allowed to stand, and the oil in the sample is aggregated by At (OH) 3 generated by the pH value of the solution.
次いで前記凝集物を濾過によって除去した後、その濾過
液中に、撹拌しながら、IOW/V%のN a OHを
1.5mA添加し、さらに充分に撹拌して、過剰分のP
ACをAt(OH)3として沈殿させ、その液中の油分
濃度を測定したところ、第1図に示す如(、、lQPP
m以下であった。Next, after removing the aggregates by filtration, 1.5 mA of IOW/V% NaOH was added to the filtrate while stirring, and the excess P was removed by further stirring.
When AC was precipitated as At(OH)3 and the oil concentration in the solution was measured, the results were as shown in Figure 1 (,,lQPP
m or less.
なお、この場合の液のP’H値は5,6であった。Note that the P'H value of the liquid in this case was 5.6.
第2図は、前記実験結果(第1図)から油分濃度とPA
C添加量との関係を示しだグラフであり、また第3図は
、同じ−く、油分濃度とPAC/NaOHとの関係をボ
したグラフである。Figure 2 shows oil concentration and PA based on the experimental results (Figure 1).
This is a graph showing the relationship between the amount of C added, and FIG. 3 is a graph showing the relationship between the oil concentration and PAC/NaOH.
また第2図中(こおける関係式1および第3図中におけ
る関係式2は、前記実験結果に基づいて作ったものであ
り、関係式i(・こおいては、任意の乳化油廃水中の油
分濃度1ogyを予め酊蛍することによシ、その乳化油
廃水に見合ったPAC添・力旧量を算・―することがで
きる。In addition, relational expression 1 in Fig. 2 (here) and relational expression 2 in Fig. 3 were created based on the above experimental results, and relational expression i (here, By pre-drying an oil concentration of 1 ogy, it is possible to calculate the appropriate amount of PAC addition/strengthening for the emulsified oil wastewater.
関′係°式2においては、過剰量PACを中和するだけ
のNaOH添加量を算出するものであって、関係式1に
おける油分濃度、PAC添加量を、関係式2に代入すれ
ばよい。In Relational Expression 2, the amount of NaOH added is calculated to neutralize the excess amount PAC, and the oil concentration and PAC addition amount in Relational Expression 1 may be substituted into Relational Expression 2.
以上の如く、本発明によれば、従来非常に複雑であった
乳化油廃水の処理を、比較的簡単に行なうことができる
。As described above, according to the present invention, the treatment of emulsified oil wastewater, which has conventionally been very complicated, can be performed relatively easily.
第1図は処理すべき乳化油廃水中の油分濃度とP A
C添加量との関係を示すグラフ、第2図は油5)濃度と
PAC添加量との関係を示すグラフ、第3図は油分濃度
とPAC/NaOHとの関係を示すグラフである。
出 辱 入 川、崎製鉄株式会社一番−4−は通
?IPAC:l加に
P^CΔνp置(ml)
第2図
第3一
覧瞭Figure 1 shows the oil concentration and PA in emulsified oil wastewater to be treated.
FIG. 2 is a graph showing the relationship between oil concentration and PAC addition amount. FIG. 3 is a graph showing the relationship between oil concentration and PAC/NaOH. Disgrace Irikawa, is Saki Steel Co., Ltd. Ichiban-4- a connoisseur? IPAC: In addition to P^CΔνp (ml) Figure 2, Figure 3.
Claims (1)
しない過剰量のポリ塩化アルミニウム溶液を添加し、そ
れによって生成する沈殿物を濾過によシ除去した後、そ
の濾過液にNaOHを添加し、過剰分として溶解してい
るポリ塩化アルミニウムを再沈殿させることを特徴とす
る乳化油廃水の処理方法。An excess amount of polyaluminum chloride solution that does not precipitate depending on the pH value of the wastewater itself is added to emulsified oil wastewater, and the resulting precipitate is removed by filtration, and then NaOH is added to the filtrate. A method for treating emulsified oil wastewater, characterized by reprecipitating polyaluminum chloride dissolved in excess.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP20770081A JPS58109189A (en) | 1981-12-21 | 1981-12-21 | Treatment for waste water of emulsified oil |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP20770081A JPS58109189A (en) | 1981-12-21 | 1981-12-21 | Treatment for waste water of emulsified oil |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS58109189A true JPS58109189A (en) | 1983-06-29 |
JPS6247432B2 JPS6247432B2 (en) | 1987-10-07 |
Family
ID=16544114
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP20770081A Granted JPS58109189A (en) | 1981-12-21 | 1981-12-21 | Treatment for waste water of emulsified oil |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS58109189A (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TW201938644A (en) * | 2018-02-23 | 2019-10-01 | 日商富士軟片股份有限公司 | Film production method, laminate production method, semiconductor device production method, and film formation composition |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS51149171A (en) * | 1975-06-17 | 1976-12-21 | Mitsubishi Chem Ind Ltd | A process for treatment of oil containing waste liquid |
JPS5246665A (en) * | 1975-10-09 | 1977-04-13 | Unitika Ltd | Process for treating an emulsifying oil-containing drain water |
JPS53105855A (en) * | 1977-02-28 | 1978-09-14 | Nippon Sekiyu Yusou Kk | Method of purifying oil contained emulsion drainage |
JPS5423189A (en) * | 1977-07-18 | 1979-02-21 | Sanyu Eng | Chlorella culturing medium |
-
1981
- 1981-12-21 JP JP20770081A patent/JPS58109189A/en active Granted
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS51149171A (en) * | 1975-06-17 | 1976-12-21 | Mitsubishi Chem Ind Ltd | A process for treatment of oil containing waste liquid |
JPS5246665A (en) * | 1975-10-09 | 1977-04-13 | Unitika Ltd | Process for treating an emulsifying oil-containing drain water |
JPS53105855A (en) * | 1977-02-28 | 1978-09-14 | Nippon Sekiyu Yusou Kk | Method of purifying oil contained emulsion drainage |
JPS5423189A (en) * | 1977-07-18 | 1979-02-21 | Sanyu Eng | Chlorella culturing medium |
Also Published As
Publication number | Publication date |
---|---|
JPS6247432B2 (en) | 1987-10-07 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP3642516B2 (en) | Method and apparatus for removing COD components in water | |
JPS58109189A (en) | Treatment for waste water of emulsified oil | |
JP4163811B2 (en) | Coagulation method and coagulant | |
JP2000263065A (en) | Removal of phosphorus in industrial waste solution | |
JPH09141274A (en) | High-degree treatment for waste water containing phosphorus | |
JPH0338294A (en) | Method for flocculation treatment of waste water | |
JP4598415B2 (en) | Organic arsenic compound processing method | |
KR100251530B1 (en) | Method of treating wastewater | |
JPH1076275A (en) | Wastewater treatment agent | |
JPS63258692A (en) | Treatment of organic sewage | |
JP2003033605A (en) | Coagulant for treatment of waste water including organic chlorine compound and treating method thereof | |
JP3501843B2 (en) | Treatment of oil-containing wastewater | |
JPH07289805A (en) | Treatment of waste water containing arsenic | |
JP2003112004A (en) | Flocculation method | |
JPH1110169A (en) | Treatment process for waste water | |
JP2000210677A (en) | Flocculating method of sludge | |
JP7168301B2 (en) | water treatment equipment | |
JP2003245675A (en) | Fluoride-ion removing method and sludge reduction method | |
KR950008376A (en) | Wastewater free discharge treatment method and system | |
JPH01176493A (en) | Treatment of waste water from incineration plant | |
JP2002320974A (en) | Removal method for dioxins | |
JPS6048189A (en) | Treatment of waste water | |
JP2000176491A (en) | Elution preventing method of phosphorus in sludge and elution preventive of phosphorus in the sludge | |
KR930012597A (en) | Wastewater treatment method containing fluorine and heavy metal | |
JPS597484B2 (en) | Coagulation method in wastewater treatment |