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JP2000301160A - Method for treating oil-containing wastewater containing surfactant - Google Patents

Method for treating oil-containing wastewater containing surfactant

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Publication number
JP2000301160A
JP2000301160A JP11109288A JP10928899A JP2000301160A JP 2000301160 A JP2000301160 A JP 2000301160A JP 11109288 A JP11109288 A JP 11109288A JP 10928899 A JP10928899 A JP 10928899A JP 2000301160 A JP2000301160 A JP 2000301160A
Authority
JP
Japan
Prior art keywords
wastewater
oil
alkaline
surfactant
acidic
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.)
Withdrawn
Application number
JP11109288A
Other languages
Japanese (ja)
Inventor
Atsushi Fujiwara
藤原  淳
Kenji Mizuarai
賢二 水洗
Kenji Hashimoto
健二 橋本
Hiroshi Koga
博 古賀
Takashi Suzuki
崇史 鈴木
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.)
Nippon Steel Corp
Tetsugen Corp
Original Assignee
Nippon Steel Corp
Tetsugen Corp
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 Nippon Steel Corp, Tetsugen Corp filed Critical Nippon Steel Corp
Priority to JP11109288A priority Critical patent/JP2000301160A/en
Publication of JP2000301160A publication Critical patent/JP2000301160A/en
Withdrawn legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PROBLEM TO BE SOLVED: To treat alkaline oil-containing wastewater containing a surfactant and acidic wastewater by one facility by mixing both in the detoxification of the alkaline wastewater containing. SOLUTION: For example, in metal surface treatment in a metal product factory, alkaline oil-containing wastewater containing a surfactant is added with pickling wastewater containing iron ions to become weakly acidic (preferably pH 4-6). The oil components, by being made weakly acidic, destroy emulsion to be separated. At the same time, the iron ions in the acidic wastewater are converted into iron hydroxide which adsorbs the separated oil components to remove them. In this way, the alkaline wastewater can be treated simultaneously with the acidic wastewater by an existing flocculation/precipitation facility so that the costs of water treating agents such as a neutralizing agent and an organic flocculant are reduced, and the installation of a floating treatment facility is obviated.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、鋼板等の表面処理
排水のうち、界面活性剤を含んだ含油排水を無害化する
処理方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a treatment method for detoxifying oil-containing wastewater containing a surfactant among surface-treated wastewater such as steel plates.

【0002】[0002]

【従来の技術】従来、金属製品工場では鋼材等の金属の
表面処理にあたり、事前に苛性ソーダ等のアルカリを用
いて脱油を行い、次に塩酸、硫酸等の酸を用いて脱錆を
行っている。脱油後の廃液は油分を含んだ濃厚アルカリ
廃液となり、また、脱油後は鋼材を水洗するため、含油
リンス排水と呼ばれる乳化した油分を含んだアルカリ性
排水が発生する。なお、洗浄効果を向上するため、通常
界面活性剤を洗浄水に添加している。同様に、脱錆後の
廃液は塩化物、硫酸化物を含んだ濃厚廃液となる。ま
た、脱錆後は鋼材を水洗するため、酸リンス排水と呼ば
れる重金属を含んだ酸性排水が発生する。
2. Description of the Related Art Conventionally, in a metal product factory, before surface treatment of metal such as steel, deoiling is performed using an alkali such as caustic soda, and then derusting is performed using an acid such as hydrochloric acid and sulfuric acid. I have. The waste liquid after deoiling becomes a concentrated alkaline waste liquid containing oil, and after deoiling, the steel material is washed with water, so that an alkaline wastewater containing emulsified oil called oil-containing rinse wastewater is generated. In order to improve the cleaning effect, a surfactant is usually added to the cleaning water. Similarly, the waste liquid after derusting becomes a concentrated waste liquid containing chlorides and sulfates. Further, after the derusting, the steel material is washed with water, so that acidic drainage containing heavy metals called acid rinse drainage is generated.

【0003】上記の金属製品工場の表面処理工程から発
生する界面活性剤を含んだアルカリ性含油排水を無害化
する処理方法としては、一般的には希硫酸添加によりp
Hを3まで下げる酸ブレーク法、または有機凝結剤添加
によるエマルジョンブレーク法により、乳化した油分を
分離し無機凝集剤に吸着させた後、pH7〜8に中和し
浮上分離し無害化処理を行っている。同様に重金属を含
有する酸性濃厚廃液及び酸性排水を無害化する処理方法
としては、一般的には消石灰、苛性ソーダ等のアルカリ
剤を排水に添加して中和し、空気曝気により二価鉄を酸
化して三価鉄の水酸化物として沈降分離し無害化処理を
行っている。
[0003] As a treatment method for detoxifying the alkaline oil-containing wastewater containing a surfactant generated from the surface treatment step of the above-mentioned metal product factory, generally, the addition of dilute sulfuric acid adds p
Emulsified oil is separated by an acid break method of lowering H to 3 or an emulsion break method by addition of an organic coagulant, adsorbed on an inorganic flocculant, neutralized to pH 7 to 8, floated and separated, and detoxified. ing. Similarly, as a treatment method for detoxifying acidic concentrated waste liquid and acidic wastewater containing heavy metals, generally, an alkaline agent such as slaked lime or caustic soda is added to the wastewater to neutralize it and oxidize divalent iron by air aeration. Then, it precipitates and separates as hydroxide of trivalent iron, and performs detoxification treatment.

【0004】すなわち、上述した従来法によるアルカリ
含油排水浮上分離処理系および酸性排水沈澱分離処理系
を示す処理系統図を図4に示す。この図に示すように、
鋼板等の表面処理工程から発生するアルカリ性含油排水
の処理は、配管輸送された排水を調整槽へ受入れ、反応
槽へ定量移送し希硫酸でpH7に中和し有機凝結剤を添
加してエマルジョンを破壊したのち、無機凝集剤添加に
より吸着し、次いで凝集槽で高分子凝集剤添加によりフ
ロックを成長させ、加圧浮上槽で浮上分離を行ない無害
な処理水として放流していた。また、浮上分離したスラ
ッジは遠心分離機で濃縮した後焼却処分していた。
[0004] That is, Fig. 4 shows a treatment system diagram showing a floatation treatment system of an alkali oil-containing wastewater and a sedimentation treatment system of an acidic wastewater by the above-mentioned conventional method. As shown in this figure,
For the treatment of alkaline oil-containing wastewater generated from the surface treatment process of steel sheets, etc., the wastewater conveyed by piping is received in a regulating tank, quantitatively transferred to a reaction tank, neutralized to pH 7 with dilute sulfuric acid, and an organic coagulant is added to form an emulsion. After destruction, it was adsorbed by the addition of an inorganic coagulant, and then the floc was grown by the addition of a polymer coagulant in a coagulation tank, floated and separated in a pressurized flotation tank, and discharged as harmless treated water. The sludge separated by flotation was concentrated by a centrifuge and then incinerated.

【0005】一方、鉄イオンを含む酸リンス排水の処理
は、配管移送された排水を調整槽に受入れ、反応槽で消
石灰添加による中和と空気曝気による二価鉄の酸化を行
い、三価鉄の水酸化物を生成し、凝集槽で高分子凝集剤
添加によりフロックを成長させた後、沈澱分離により無
害化処理を行っていた。また、凝集汚泥は別途脱水処理
を行い、高炉原料としてリサイクルしている。
On the other hand, in the treatment of acid rinse wastewater containing iron ions, wastewater transferred to a pipe is received in a regulating tank, neutralization is performed by adding slaked lime in a reaction tank, and oxidation of divalent iron is performed by aeration with air. The hydroxide was produced, and floc was grown by adding a polymer flocculant in a flocculation tank, and then detoxification treatment was performed by precipitation separation. The coagulated sludge is separately dehydrated and recycled as a raw material for the blast furnace.

【0006】[0006]

【発明が解決しようとする課題】上述したように、溶接
用缶材料や自動車用鋼板を製造する金属製品工場におい
ては、それぞれの用途に応じた鋼板等の金属板の表面処
理を行っており、表面処理工程から発生する廃液および
排水は、アルカリ性含油排水を中和凝集浮上分離処理
で、酸リンス排水を中和凝集沈澱分離処理で無害化処理
している。このように、アルカリ性含油排水と酸リンス
排水は同時に処理することができず各々別の処理設備を
設けて排水処理を行っているのが現状である。
As described above, in metal product factories that manufacture welding can materials and steel plates for automobiles, surface treatments of metal plates such as steel plates are performed according to each application. Wastewater and wastewater generated from the surface treatment step are treated to neutralize the alkaline oil-containing wastewater by neutralization coagulation flotation separation treatment, and the acid rinse wastewater by neutralization coagulation sedimentation separation treatment. As described above, the alkaline oil-containing wastewater and the acid rinse wastewater cannot be treated simultaneously, and at present, wastewater treatment is performed by providing separate treatment facilities.

【0007】このため、次のような問題がある。 (イ)アルカリ性含油排水には希硫酸等の酸剤、酸排水
には消石灰等のアルカリ剤が中和剤として必要である。 (ロ)アルカリ性含油排水の油分処理には、酸ブレーク
方式では過剰の酸剤、またはエマルジョンブレーク方式
では有機凝結剤が必要であり、かつポリ塩化アルミニウ
ム等の無機凝集剤が必要である。 (ハ)生成フロックの比重の違いにより、アルカリ性含
油排水では浮上分離方式、酸リンス排水では沈降分離方
式を採用するため別々の処理設備が必要である。
For this reason, there are the following problems. (A) An acid agent such as dilute sulfuric acid is required as an alkaline oil-containing wastewater, and an alkali agent such as slaked lime is required as a neutralizer as an acid wastewater. (B) The oil treatment of the alkaline oil-containing wastewater requires an excess acid agent in the acid break system or an organic coagulant in the emulsion break system and an inorganic coagulant such as polyaluminum chloride. (C) Due to the difference in the specific gravity of the generated floc, separate treatment equipment is required to adopt the floatation separation method for alkaline oil-containing wastewater and the sedimentation separation method for acid rinse wastewater.

【0008】上記のように、現状ではアルカリ性含油排
水と酸リンス排水を処理するには、別々の処理設備や中
和剤、有機凝結剤等の水処理薬剤を必要とするなど、経
済的ではない。そこで、本発明では、このような問題を
解消し、酸リンス排水処理設備を利用して表面処理工程
から発生するアルカリ性含油排水と酸性排水の全てを、
一つの設備で処理する方法を提供するものである。
As described above, at present, it is not economical to treat alkaline oil-containing wastewater and acid rinse wastewater, because separate treatment facilities and water treatment chemicals such as neutralizing agents and organic coagulants are required. . Therefore, in the present invention, such problems are solved, and all of the alkaline oil-containing wastewater and the acidic wastewater generated from the surface treatment step using the acid rinse wastewater treatment equipment,
The purpose of the present invention is to provide a method of processing with one facility.

【0009】[0009]

【課題を解決するための手段】その発明の要旨とすると
ころは、 (1)界面活性剤を含んだアルカリ性含油排水を無害化
処理する方法において、該排水を鉄イオンを含んだ酸性
排水と混合することによって、油分を分離し水酸化物に
吸着させ凝集沈澱させることを特徴とする界面活性剤を
含む含油排水の処理方法。 (2)アルカリ性含油排水と酸性排水を、調整槽で弱酸
に調整することを特徴とする前記(1)記載の界面活性
剤を含む含油排水の処理方法。
The gist of the invention is as follows: (1) In a method for detoxifying an alkaline oil-containing wastewater containing a surfactant, the wastewater is mixed with an acidic wastewater containing iron ions. A method for treating oil-containing wastewater containing a surfactant, comprising separating oil, adsorbing it to a hydroxide, and causing coagulation and precipitation. (2) The method for treating oil-containing wastewater containing a surfactant according to the above (1), wherein the alkaline oil-containing wastewater and the acidic wastewater are adjusted to a weak acid in a regulating tank.

【0010】(3)弱酸がpH4〜6であることを特徴
とする前記(2)記載の界面活性剤を含む含油排水の処
理方法。 (4)反応槽にて消石灰等のアルカリ剤にてpH7まで
中和し、かつ空気曝気にて酸化したのち、凝集沈澱を行
うことを特徴とする前記(1)〜(3)記載の界面活性
剤を含む含油排水の処理方法にある。
(3) The method for treating oil-containing wastewater containing a surfactant according to the above (2), wherein the weak acid has a pH of 4 to 6. (4) The surface activity according to the above (1) to (3), wherein neutralization is performed to pH 7 with an alkali agent such as slaked lime in a reaction tank, oxidation is performed by air aeration, and coagulation precipitation is performed. In a method for treating oil-containing wastewater containing an agent.

【0011】[0011]

【発明の実施の形態】以下、本発明について詳細に説明
する。本発明者らは、種々研究を重ねた結果、界面活性
剤を含有するアルカリ性含油排水に、鉄イオンを含む酸
リンス排水を添加して弱酸(好ましくはpH4〜6)に
することにより、含油排水中に含有する油分が分離し鉄
の水酸化物に吸着され、従来困難であったアルカリ性含
油排水と酸性排水を同時に固液分離処理(凝集沈澱処
理)することが可能であることを見出した。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail. The present inventors have conducted various studies, and as a result, by adding an acid rinse containing iron ions to an alkaline oil-containing wastewater containing a surfactant to make it a weak acid (preferably pH 4 to 6), the oil-containing wastewater can be obtained. It has been found that the oil contained therein is separated and adsorbed by the hydroxide of iron, and it is possible to simultaneously perform the solid-liquid separation treatment (coagulation sedimentation treatment) on the alkaline oil-containing wastewater and the acidic wastewater, which were difficult in the past.

【0012】すなわち、従来は酸ブレーク方式の場合、
pH3の強酸にまでpHを下げることにより乳化した油
分の分離を行い、無機凝集剤(主にポリ塩化アルミニウ
ム)にて吸着除去していたものが、本発明者等の研究の
結果、酸リンス排水中に含まれる水素イオンおよび鉄イ
オンを利用して除去できることが判明した。アルカリ性
含油排水中の油分は、酸性排水と混合し弱酸(好ましく
はpH4〜6)にすることによりエマルジョンが破壊さ
れ分離する。同時に酸性排水中の鉄イオンが水酸化物を
生成し、その水酸化物に分離した油分が吸着され除去さ
れる。次に、消石灰等のアルカリ剤によりpH7まで中
和し、空気曝気による酸化により、鉄イオンの利用効率
を高め、高分子凝集剤添加によりフロックを成長させた
後、沈澱分離処理することができる。
That is, conventionally, in the case of the acid break system,
Separation of emulsified oil by lowering the pH to a strong acid of pH 3 and removal by adsorption with an inorganic flocculant (mainly polyaluminum chloride) resulted in acid rinse drainage as a result of research conducted by the present inventors. It has been found that hydrogen ions and iron ions contained therein can be removed. The oil in the alkaline oil-containing wastewater is mixed with an acidic wastewater to make a weak acid (preferably pH 4 to 6), whereby the emulsion is broken and separated. At the same time, iron ions in the acidic wastewater generate hydroxides, and the oil separated into the hydroxides is adsorbed and removed. Next, it is neutralized to pH 7 with an alkali agent such as slaked lime, the efficiency of use of iron ions is increased by oxidation by air aeration, and floc is grown by adding a polymer flocculant.

【0013】[0013]

【実施例】以下、本発明について、さらに実施例によっ
て具体的に説明する。図1は、本発明に係る界面活性剤
を含むアルカリ性含油排水および酸リンス排水処理の混
合処理の処理形態を示す図である。この図に示すよう
に、アルカリ性含油排水と酸リンス排水の混合後のpH
はその混合比により変化するが、そのpHと処理水の油
分濃度の関係を図2に示す。図2は横軸が混合後のpH
であり、縦軸が処理水中の油分濃度(mg/l)を表し
ている。図2から判るようにpHが酸領域から中和領域
まで全て処理水中の油分濃度は排水基準(5mg/l未
満)をクリヤーしており、特に強酸性領域で酸ブレーク
しなくても、油分除去が可能なことが立証できた。
EXAMPLES Hereinafter, the present invention will be described more specifically with reference to examples. FIG. 1 is a view showing a processing mode of a mixing treatment of an alkaline oil-containing wastewater containing a surfactant and an acid rinse wastewater treatment according to the present invention. As shown in this figure, pH after mixing of alkaline oil-containing wastewater and acid rinse wastewater
Varies depending on the mixing ratio, and the relationship between the pH and the oil concentration of the treated water is shown in FIG. Figure 2 shows the pH after mixing on the horizontal axis.
And the vertical axis represents the oil concentration (mg / l) in the treated water. As can be seen from FIG. 2, the oil concentration in the treated water is clear from the drainage standard (less than 5 mg / l) from the acid region to the neutralized region. Has been proved to be possible.

【0014】また、水酸化鉄で油分を吸着させるため、
フロック沈降速度が低下し処理水にキャリーオーバーす
る恐れがあるが、その沈降速度と混合pHは図3の関係
を見出すことができた。すなわち、図3は横軸が混合p
Hであり、縦軸に沈降速度(m/H)を表している。こ
の図3から判るように、混合pHにより沈降速度に影響
がでるが、これはpHが低いと再中和に使用する消石灰
の量が増加しSS負荷が増加するため、沈降速度が速く
なることが判明した。ただし、一般的に通常凝集沈降設
備の表面負荷は約1m/Hであり、十分に余裕があるた
め、処理には特に問題となっていない。
In order to adsorb oil with iron hydroxide,
There is a possibility that the floc sedimentation speed may decrease and carry over to the treated water. The relationship between the sedimentation speed and the mixing pH can be found in FIG. That is, FIG.
H, and the vertical axis represents the sedimentation velocity (m / H). As can be seen from FIG. 3, the sedimentation velocity is affected by the mixed pH. This is because if the pH is low, the amount of slaked lime used for re-neutralization increases and the SS load increases, so that the sedimentation velocity increases. There was found. However, in general, the surface load of the coagulation and sedimentation equipment is about 1 m / H, and there is a sufficient margin, so there is no particular problem in the treatment.

【0015】この混合処理をした結果、従来はアルカリ
性含油排水処理に使用していた有機凝結剤および無機凝
集剤が不要となり、相互中和により中和剤の希硫酸およ
び消石灰の使用量が減少した。また、無機凝集剤の使用
が不要となったため、無機凝集剤に起因するスラッジ発
生量が減少し、かつ従来の焼却処分から高炉原料へのリ
サイクルが可能となった。なお、浮上処理設備を休止で
きるため設備のメンテナンス費用が不要となった。図1
に示す処理を行った結果の処理水性状を表1に示す。
As a result of this mixing treatment, the organic coagulant and the inorganic coagulant conventionally used for the alkaline oil-containing wastewater treatment become unnecessary, and the mutual neutralization reduces the amount of the dilute sulfuric acid and slaked lime used as the neutralizing agent. . In addition, since the use of an inorganic coagulant is not required, the amount of sludge generated by the inorganic coagulant is reduced, and recycling from conventional incineration to raw material for a blast furnace becomes possible. In addition, since the floating processing equipment can be stopped, the maintenance cost of the equipment is not required. FIG.
Table 1 shows the treatment aqueous properties as a result of the treatment shown in Table 1.

【0016】[0016]

【表1】 [Table 1]

【0017】表1に示すように、本発明の方法によれ
ば、アルカリ性含油排水を酸性排水と混合処理すること
が可能であり、処理水性状も排水基準を十分に満たすこ
とができる。また、従来の処理方法と本発明の方法を処
理性で比較した結果を表2に示す。表2の結果から判る
ように、本発明の方法によればアルカリ性含油排水処理
用の有機凝結剤および無機凝集剤が不要となり、かつ中
和剤が減少した結果、排水の単位あたりの薬剤使用量が
減り、発生汚泥(脱水ケーキ)の減量化およびコスト削
減に寄与している。
As shown in Table 1, according to the method of the present invention, the alkaline oil-containing wastewater can be mixed with the acidic wastewater, and the treated water quality can sufficiently satisfy the wastewater standards. Table 2 shows the results of comparison between the conventional processing method and the method of the present invention in terms of processing performance. As can be seen from the results in Table 2, according to the method of the present invention, an organic coagulant and an inorganic coagulant for treating an alkaline oil-containing wastewater are not required, and the amount of the neutralizing agent is reduced. And contribute to the reduction of the amount of generated sludge (dewatered cake) and cost reduction.

【0018】[0018]

【表2】 [Table 2]

【0019】[0019]

【発明の効果】以上述べたように、本発明の方法によれ
ば、界面活性剤を含んだアルカリ性含油排水を、鉄イオ
ンを含む酸性排水と既存の凝集沈澱処理設備で同時に処
理することが可能であり、中和剤、有機凝結剤等の水処
理薬剤コストの削減と浮上処理設備の新設が不要になる
ことから、経済効果があがることはいうまでもない。
As described above, according to the method of the present invention, it is possible to simultaneously treat an alkaline oil-containing wastewater containing a surfactant with an acidic wastewater containing iron ions by an existing coagulation-sedimentation treatment facility. It goes without saying that the cost reduction of water treatment chemicals such as a neutralizing agent and an organic coagulant and the necessity of newly installing a flotation treatment facility are eliminated, so that the economic effect is improved.

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

【図1】本発明に係る界面活性剤を含むアルカリ性含油
排水および酸リンス排水処理の混合処理の処理形態を示
す図、
FIG. 1 is a diagram showing a treatment form of a mixing treatment of an alkaline oil-containing wastewater containing a surfactant and an acid rinse wastewater treatment according to the present invention;

【図2】混合排水のpHと処理水油分濃度との関係を示
す図、
FIG. 2 is a diagram showing the relationship between the pH of mixed wastewater and the concentration of treated water oil,

【図3】混合排水のpHと凝集汚泥沈降速度との関係を
示す図、
FIG. 3 is a diagram showing the relationship between the pH of mixed wastewater and the settling rate of coagulated sludge,

【図4】従来法によるアルカリ含油排水浮上分離処理系
および酸性排水沈澱分離処理系を示す処理系統図であ
る。
FIG. 4 is a treatment system diagram showing an alkali oil-containing wastewater floating separation treatment system and an acidic wastewater sedimentation separation treatment system according to a conventional method.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 1/66 540 C02F 1/66 540H (72)発明者 水洗 賢二 愛知県東海市東海町2丁目3番14号 株式 会社鐵原名古屋支店内 (72)発明者 橋本 健二 愛知県東海市東海町5−3 新日本製鐵株 式会社名古屋製鐵所内 (72)発明者 古賀 博 愛知県東海市東海町5−3 新日本製鐵株 式会社名古屋製鐵所内 (72)発明者 鈴木 崇史 愛知県東海市東海町5−3 新日本製鐵株 式会社名古屋製鐵所内 Fターム(参考) 4D062 BA19 BA21 BB12 CA06 CA07 DA12 DA39 DC02 DC06 EA04 EA06 EA13 EA17 EA32 FA01 FA25 FA28 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) C02F 1/66 540 C02F 1/66 540H (72) Inventor Kenji Mizurai 2-3-3 Tokaicho, Tokai City, Aichi Prefecture No. 14 Inside Tehara original Nagoya branch (72) Inventor Kenji Hashimoto 5-3 Tokai-cho, Tokai-shi, Aichi Prefecture Inside Nippon Steel Corporation Nagoya Works (72) Inventor Hiroshi Koga 5 Tokai-cho, Tokai-shi, Aichi prefecture -3 Inside Nippon Steel Corporation Nagoya Works (72) Inventor Takashi Suzuki 5-3 Tokaicho, Tokai City, Aichi Prefecture F-term in Nagoya Works Nippon Steel Corporation 4D062 BA19 BA21 BA21 BB12 CA06 CA07 DA12 DA39 DC02 DC06 EA04 EA06 EA13 EA17 EA32 FA01 FA25 FA28

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 界面活性剤を含んだアルカリ性含油排水
を無害化処理する方法において、該排水を鉄イオンを含
んだ酸性排水と混合することによって、油分を分離し水
酸化物に吸着させ凝集沈澱させることを特徴とする界面
活性剤を含む含油排水の処理方法。
In a method for detoxifying an alkaline oil-containing wastewater containing a surfactant, the wastewater is mixed with an acidic wastewater containing iron ions to separate an oil component, adsorb it to a hydroxide, and cause coagulation and sedimentation. A method for treating oil-containing wastewater containing a surfactant.
【請求項2】 アルカリ性含油排水と酸性排水を、調整
槽で弱酸に調整することを特徴とする請求項1記載の界
面活性剤を含む含油排水の処理方法。
2. The method for treating oil-containing wastewater containing a surfactant according to claim 1, wherein the alkaline oil-containing wastewater and the acidic wastewater are adjusted to a weak acid in a regulating tank.
【請求項3】 弱酸がpH4〜6であることを特徴とす
る請求項2記載の界面活性剤を含む含油排水の処理方
法。
3. The method for treating oil-containing wastewater containing a surfactant according to claim 2, wherein the weak acid has a pH of 4 to 6.
【請求項4】 反応槽にて消石灰等のアルカリ剤にてp
H7まで中和し、かつ空気曝気にて酸化したのち、凝集
沈澱を行うことを特徴とする請求項1〜3記載の界面活
性剤を含む含油排水の処理方法。
4. In a reaction tank, p is added with an alkaline agent such as slaked lime.
The method for treating oil-containing wastewater containing a surfactant according to any one of claims 1 to 3, wherein the mixture is neutralized to H7 and oxidized by air aeration, and then coagulated and precipitated.
JP11109288A 1999-04-16 1999-04-16 Method for treating oil-containing wastewater containing surfactant Withdrawn JP2000301160A (en)

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Cited By (6)

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Publication number Priority date Publication date Assignee Title
US6409927B1 (en) * 1998-06-03 2002-06-25 Enrique-Ruben Cardenas-Granguillhome Process for the treatment of polluted metal-mechanic industrial wastewater and urban water
JP2010274244A (en) * 2009-06-01 2010-12-09 Nippon Steel Corp Method for clarifying treatment of steel production waste water
CN102276122A (en) * 2011-07-27 2011-12-14 北京京诚科林环保科技有限公司 Denitrification treatment process for stainless steel cold rolling mixed acid wastewater
CN103723853A (en) * 2013-12-04 2014-04-16 江苏双净净化科技有限公司 Intermittent comprehensive treating system for gas generating station and treating method of intermittent comprehensive treating system
CN109851102A (en) * 2019-04-17 2019-06-07 中和环境工程有限公司 A kind of processing method of graphite acid waste water Fractional Collections and segmentation neutralization
CN114275972A (en) * 2021-12-28 2022-04-05 中冶南方工程技术有限公司 Low-cost resource utilization process for acidic wastewater

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6409927B1 (en) * 1998-06-03 2002-06-25 Enrique-Ruben Cardenas-Granguillhome Process for the treatment of polluted metal-mechanic industrial wastewater and urban water
JP2010274244A (en) * 2009-06-01 2010-12-09 Nippon Steel Corp Method for clarifying treatment of steel production waste water
CN102276122A (en) * 2011-07-27 2011-12-14 北京京诚科林环保科技有限公司 Denitrification treatment process for stainless steel cold rolling mixed acid wastewater
CN103723853A (en) * 2013-12-04 2014-04-16 江苏双净净化科技有限公司 Intermittent comprehensive treating system for gas generating station and treating method of intermittent comprehensive treating system
CN103723853B (en) * 2013-12-04 2015-08-26 江苏双净净化科技有限公司 Gas generating station intermittent type total system and treatment process thereof
CN109851102A (en) * 2019-04-17 2019-06-07 中和环境工程有限公司 A kind of processing method of graphite acid waste water Fractional Collections and segmentation neutralization
CN109851102B (en) * 2019-04-17 2021-11-23 中和环境工程有限公司 Treatment method for sectional collection and sectional neutralization of graphite acid wastewater
CN114275972A (en) * 2021-12-28 2022-04-05 中冶南方工程技术有限公司 Low-cost resource utilization process for acidic wastewater

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