JP2001137839A - Method for treating waste water containing solid content - Google Patents

Method for treating waste water containing solid content

Info

Publication number
JP2001137839A
JP2001137839A JP32439399A JP32439399A JP2001137839A JP 2001137839 A JP2001137839 A JP 2001137839A JP 32439399 A JP32439399 A JP 32439399A JP 32439399 A JP32439399 A JP 32439399A JP 2001137839 A JP2001137839 A JP 2001137839A
Authority
JP
Japan
Prior art keywords
oil
waste water
wastewater
solid content
solids
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Withdrawn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
JP32439399A
Other languages
Japanese (ja)
Inventor
Katsumi Omori
克己 大森
Tatsuya Yamauchi
辰也 山内
Mitsuhiro Ohashi
満広 大橋
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.)
Eneos Corp
Original Assignee
Japan Energy 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 Japan Energy Corp filed Critical Japan Energy Corp
Priority to JP32439399A priority Critical patent/JP2001137839A/en
Publication of JP2001137839A publication Critical patent/JP2001137839A/en
Withdrawn legal-status Critical Current

Links

Landscapes

  • Physical Water Treatments (AREA)
  • Removal Of Floating Material (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for treating waste water for efficiently removing solid contents from waste water in which solid contents are diffused, especially, waste water containing oil in which the solid contents are diffused in a stable state like fine grains. SOLUTION: In this method for treating waste water, hydrocarbon oil is mixed to waste water containing solid contents and then statically placed so as to be divided into a water layer and an oil layer. As a result, it is possible to efficiently remove the solid contents from the waste water, and to surely treat waste water containing oil in which the solid contents are diffused in a stable state like fine grains.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、排水から固形分を除去
する排水の処理方法に関し、特には、石油精製工程など
から発生する微粒子状の固形分を含む含油排水からその
固形分を除去する排水の処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wastewater treatment method for removing solids from wastewater, and more particularly to a method for removing solids from oil-containing wastewater containing fine solids generated from a petroleum refining process or the like. The present invention relates to a method for treating wastewater.

【0002】[0002]

【従来の技術】従来、排水中の固形分は、濾過、遠心分
離、静置などの方法で除去されており、また、このよう
な方法でその大部分は除去されていた。しかし、固形分
が微粒子状の場合、排水中に安定に分散し、長期間静置
しても凝集や沈殿が得られず、また、濾過や遠心分離を
行っても効率的に、十分除去することは非常に困難であ
る。特に、石油精製における原油の脱塩工程からの排
水、あるいは、各種の接触処理工程から発生する排水な
どには、微粒子状の固形分とともに油分として鉱油分が
含まれるため、該固形分は油分との相互作用により更に
安定な状態で分散している。また、食品加工においても
その加工工程などからの排水について、固形分と油分と
して油脂分が含まれるものがあるため、同様な問題を抱
えている。
2. Description of the Related Art Conventionally, solids in waste water have been removed by a method such as filtration, centrifugation, or standing, and most of them have been removed by such a method. However, when the solid content is in the form of fine particles, the solid content is stably dispersed in the waste water, and aggregation or precipitation is not obtained even when left for a long period of time. In addition, even if filtration or centrifugation is performed, it is efficiently and sufficiently removed. It is very difficult. In particular, wastewater from the desalting step of crude oil in petroleum refining, or wastewater generated from various contact treatment steps, etc., contains mineral oil as oil along with fine solids. Are dispersed in a more stable state due to the interaction of Further, in the case of food processing, wastewater from the processing step or the like has a similar problem because some fats and oils are contained as solids and oils.

【0003】[0003]

【発明が解決しようとする課題】このように固形分を安
定な分散状態で含有する排水は、沈澱池で長時間静置し
ても固形分や油分が十分に分離されず、結局、面倒で高
コストな別の処理を行わねばならず、排水処理全体の負
担を増していた。したがって、このような排水であって
も、固形分を効率的に分離することができる排水の処理
方法が求められている。本発明は、上述の問題を解決す
るものであり、固形分が分散されて含有される排水か
ら、特に微粒子状で安定な状態で分散されている含油排
水から効率的に該固形分を除去する排水の処理方法を提
供することを課題とするものである。
The wastewater containing solids in a stable dispersed state as described above does not sufficiently separate solids and oil even if left in a sedimentation basin for a long period of time. Separate high-cost treatment had to be performed, increasing the overall burden on wastewater treatment. Accordingly, there is a need for a method for treating wastewater that can efficiently separate solids even with such wastewater. The present invention solves the above-mentioned problems, and efficiently removes solids from wastewater containing solids dispersed therein, particularly oil-containing wastewater dispersed in a stable state in the form of fine particles. It is an object to provide a method for treating wastewater.

【0004】[0004]

【課題を解決するための手段】本発明者らは、固形分を
効率的に除去する排水の処理方法の研究を進めるなか
で、排水に炭化水素油を混合すると、固形分が水層から
油槽に選択的に移行することを見出し、本発明に想到し
た。すなわち、本発明の固形分を含有する排水の処理方
法は、固形分を分散状態で含有する排水に炭化水素油を
混合した後、静置により水層と油層に分離することを特
徴とする。本発明によれば、固形分が分散した排水に、
炭化水素油を混合した後、静置して水層と油層に分離す
ると、固形分は炭化水素油側に選択的に移って、移行し
た固形分を分散された状態で含有する油層と、固形分が
除去された排水の水層に容易に分離することができる。
特に、微粒子状の固形分が排水中に油分やフェノールな
どの油溶性の不純物等との相互作用によってより安定に
分散して含まれている場合、炭化水素油を混合すること
によって安定が崩れて排水中の油分や不純物等はこの炭
化水素油に移行するので、排水中の油分及び不純物の濃
度も、固形分とともに低下する。
Means for Solving the Problems In the course of research on a wastewater treatment method for efficiently removing solids, the present inventors have found that when hydrocarbon oil is mixed into the wastewater, the solids are removed from the water layer into an oil tank. And found the present invention, and came to the present invention. That is, the method for treating wastewater containing solid content according to the present invention is characterized in that hydrocarbon oil is mixed with wastewater containing solid content in a dispersed state, and then separated into an aqueous layer and an oil layer by standing. According to the present invention, the wastewater in which the solid content is dispersed,
After the hydrocarbon oil is mixed, the mixture is allowed to stand and separated into an aqueous layer and an oil layer.The solid content is selectively transferred to the hydrocarbon oil side, and an oil layer containing the transferred solid content in a dispersed state, It can be easily separated into the water layer of the waste water from which the waste has been removed.
In particular, when the particulate solids are more stably dispersed and contained in the waste water by interaction with oil-soluble impurities such as oil and phenol, the stability is lost by mixing the hydrocarbon oil. Since oil and impurities in the wastewater migrate to the hydrocarbon oil, the concentrations of the oil and impurities in the wastewater also decrease with the solid content.

【0005】[0005]

【好ましい実施の態様】本発明でいう固形分とは、排水
中に分散状態で含有される固体の不溶成分である。この
ような固形分を含む産業排水であれば、どのような排水
に対しても本発明の方法は有効に適用できる。具体的な
例としては、石油精製工程において、原油中に含まれる
不溶性の有機物、無機物、これらの混合物(例えば、ス
ラッジ)、触媒の破砕粉などが挙げられる。本発明は、
固形分のサイズを特に限定するものではないが、平均粒
径が100μm以下のものに好ましく、特に1〜10μ
mのものは沈降しにくく濾過することも困難であるが、
これらにも有効に適用できる。排水中に占める固形分の
量は、10ppm以上が好ましく、100ppm以上含まれる
場合、本発明は特に有効である。なお、固形分の重量
は、例えば、10μmのフィルタで濾過し、トルエンで
洗浄して残った成分として定量することができる。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The solid content referred to in the present invention is a solid insoluble component contained in a dispersed state in waste water. The method of the present invention can be effectively applied to any type of industrial wastewater containing solids. Specific examples include insoluble organic and inorganic substances, a mixture thereof (eg, sludge), and crushed powder of a catalyst contained in crude oil in a petroleum refining process. The present invention
Although the size of the solid content is not particularly limited, it is preferable that the average particle size is 100 μm or less, and particularly 1 to 10 μm.
m are difficult to settle and difficult to filter,
It can be applied effectively to these. The amount of the solid content in the wastewater is preferably 10 ppm or more, and when the amount is 100 ppm or more, the present invention is particularly effective. In addition, the weight of the solid content can be quantified as a component remaining after filtration with a 10 μm filter and washing with toluene, for example.

【0006】本発明で処理対象とする排水としては、上
述の固形分を含むものであれば、特に限定されるもので
はない。特に排水が油分を含んでいる場合、本発明は更
に効果的である。例えば、石油精製工程の排水、食品加
工工程の排水に同伴されはる油分や油脂分は、固形分を
排水中に安定な状態で分散する作用を有する。このた
め、一般的にこのような油分等を含有する排水から固形
分を分離することはより困難になるが、本発明によれば
排水から容易に分離することができる。具体的には、油
分や油脂分などの親油性成分が排水中に0.001重量
%以上、特には0.01〜1重量%含まれる場合、本発
明は効果的である。また、本発明は、フェノールなどの
油溶性の有機物を含有する排水処理にも有効であり、こ
れらの濃度を低減することができる。
The wastewater to be treated in the present invention is not particularly limited as long as it contains the above-mentioned solid content. The present invention is more effective especially when the drainage contains oil. For example, oils and fats and oils entrained in the wastewater of the oil refining process and the wastewater of the food processing process have an effect of dispersing solid components in the wastewater in a stable state. For this reason, it is generally more difficult to separate solids from wastewater containing such oils and the like, but according to the present invention, solids can be easily separated from wastewater. Specifically, the present invention is effective when the effluent contains 0.001% by weight or more, particularly 0.01 to 1% by weight of a lipophilic component such as an oil component or a fat component. The present invention is also effective for wastewater treatment containing oil-soluble organic substances such as phenol, and can reduce the concentration of these substances.

【0007】本発明に用いる炭化水素油は、排水と油分
を静置して効率良く分離するためには、比重が0.95
以下のものが好ましく、特に0.90以下の炭化水素油
を用いることが好ましい。あまり軽質な炭化水素油は、
安全上の問題があるので、この観点で比重が0.70以
上のものが好ましい。また、この炭化水素油は精製され
たものを用いる必要はなく、また固形分、水分を含んで
いても良い。このような油として、具体的には、石油精
製における原油、重質ナフサ、灯油、軽油、重油、潤滑
油、及びそれらに相当する石油留分の中間製品又は副製
品あるいはそれらの混合油などが挙げられ、また、原油
タンカーの洗浄回収油や石油精製工程で発生する廃油、
スロップオイル、洗浄油なども用いることができる。
The specific gravity of the hydrocarbon oil used in the present invention is 0.95 in order to allow the waste water and the oil component to stand and separate efficiently.
The following are preferable, and it is particularly preferable to use a hydrocarbon oil of 0.90 or less. Not very light hydrocarbon oils
From the viewpoint of safety, those having a specific gravity of 0.70 or more are preferable. It is not necessary to use a refined hydrocarbon oil, and the hydrocarbon oil may contain solids and moisture. Specific examples of such oils include crude oils in petroleum refining, heavy naphtha, kerosene, light oil, heavy oil, lubricating oils, and intermediate products or by-products of the corresponding petroleum fractions or mixed oils thereof. And the oil recovered from washing and recovery of crude oil tankers and waste oil generated in the oil refining process.
Slop oil, washing oil and the like can also be used.

【0008】本発明において、排水と炭化水素油の混合
は、どのような方法で行っても良く、例えば、攪拌槽で
攪拌翼、ジェット流などを用いる方法、ミキシングバル
ブ、インラインミキサなどを用いる方法など周知の方法
を適宜選択して行えばよい。混合時の温度としては、粘
度を下げて混合の効率を高めるために排水と炭化水素油
の両者又はいずれか一方を加熱して、40〜90℃、更
には50〜70℃で混合することが好ましい。混合時間
は、混合の方法にもよるが、1分以上、特には3〜20
分が排水と炭化水素油との接触を十分行わせるために好
ましい。排水と炭化水素油の混合割合は、排水1容量部
に対して炭化水素油を0.1容量部以上、特には0.2
〜0.6容量部混合することが好ましい。
In the present invention, mixing of the waste water and the hydrocarbon oil may be performed by any method, for example, a method using a stirring blade or a jet flow in a stirring tank, a method using a mixing valve, an in-line mixer, or the like. Such a known method may be appropriately selected and performed. As the temperature at the time of mixing, in order to lower the viscosity and increase the efficiency of mixing, the wastewater and / or the hydrocarbon oil may be heated and mixed at 40 to 90 ° C, further 50 to 70 ° C. preferable. The mixing time depends on the mixing method, but is 1 minute or more, especially 3 to 20 minutes.
The amount is preferable in order to make sufficient contact between the waste water and the hydrocarbon oil. The mixing ratio of the wastewater and the hydrocarbon oil is such that the hydrocarbon oil is at least 0.1 part by volume, especially 0.2 part
It is preferred to mix up to 0.6 parts by volume.

【0009】排水と炭化水素油の混合物は、静置するこ
とにより水層と油層に重力分離される。静置分離は、油
槽等に回分式に一定時間保って分離する方法や油槽の入
口と出口にある間隔をとってそこを通過する間に分離す
る連続的な方法などを用いて行うことができる。連続的
な方法を利用した分離装置としては、例えば、APIオ
イルセパレータ、PPIオイルセパレータ、CPIオイ
ルセパレータなどの静置型分離槽が挙げられる。なお、
遠心力による強制的な分離を行うことは、一旦油側に移
行した固形分が水側に戻るおそれがあるので、排水から
固形分を取り除くことを目的とする本発明には好ましく
ない。また、水層と油層の分離を容易にするためにエマ
ルジョンブレーカを添加することもできる。エマルジョ
ンブレーカとしては、陽イオン性のものが好ましい。
The mixture of the waste water and the hydrocarbon oil is separated by gravity into an aqueous layer and an oil layer by standing. The stationary separation can be performed using a method of separating the oil tank or the like while keeping it batchwise for a certain period of time, or a continuous method of separating the oil tank while passing through an inlet and an outlet at a certain interval. . Examples of a separation apparatus using a continuous method include a stationary separation tank such as an API oil separator, a PPI oil separator, and a CPI oil separator. In addition,
Forcible separation by centrifugal force is not preferred in the present invention, which aims at removing solids from wastewater, since the solids once transferred to the oil side may return to the water side. Further, an emulsion breaker can be added to facilitate separation of the water layer and the oil layer. As the emulsion breaker, a cationic breaker is preferable.

【0010】このようにして本発の方法で処理された排
水は、水層として分離され、固形分を殆ど含まず、また
油溶性の有機不純物(油分、油脂分及びフェノール分な
ど)の濃度も低下している。一方、混合した炭化水素油
は油層として分離回収される。回収された炭化水素油
は、 (1)リサイクルして排水処理に再度利用する (2)原油などの石油精製の原料と混合して精製処理
し、石油製品を得る (3)石油精製の加熱炉やボイラの燃料(自家消費燃
料)、あるいは熱分解装置の原料として使用する などに利用することができる。固形分は、比較的比重の
小さい油層に移行しているので、遠心分離などによって
容易に濃縮、分離できる。炭化水素油をリサイクル使用
する場合には、このように固形分を除いて繰り返し用い
ることができる。また、油層として回収した炭化水素油
を精製処理する場合は、固形分が含まれていても、蒸留
される際に重質油側に移行してゆき、アスファルトや重
油に含まれることになるので、特に固形分を除去する必
要はない。遠心分離して固形分を除いた後に精製処理し
てもよいことはいうまでもない。
The wastewater treated by the method of the present invention is separated as an aqueous layer, contains almost no solid matter, and has a low concentration of oil-soluble organic impurities (such as oil, fat and phenol). Is declining. On the other hand, the mixed hydrocarbon oil is separated and recovered as an oil layer. The recovered hydrocarbon oil is (1) recycled and reused for wastewater treatment. (2) Refined by mixing with petroleum refining raw materials such as crude oil to obtain petroleum products. (3) Heating furnace for petroleum refining It can be used as fuel for boilers and boilers (self-consumed fuel), or as a raw material for pyrolysis equipment. Since the solid content has moved to an oil layer having a relatively small specific gravity, it can be easily concentrated and separated by centrifugation or the like. When the hydrocarbon oil is recycled, it can be repeatedly used except for the solid content. Also, when refining hydrocarbon oil recovered as an oil layer, even if it contains solids, it will migrate to heavy oil when distilled, and will be contained in asphalt and heavy oil. It is not particularly necessary to remove solids. Needless to say, purification treatment may be performed after removing solids by centrifugation.

【0011】[0011]

【実施例】以下、実施例に基づき本発明をより具体的に
説明する。
Hereinafter, the present invention will be described more specifically based on examples.

【0012】(実施例)平均粒子径10μmの固形物を
100重量ppm、油分を100重量ppm、及びその他の有
機物はフェノール類として10重量ppm含有する原油の
脱塩槽排水に、炭化水素油として軽油を、前記排水1容
量部に対して0.2容量部の割合で攪拌槽に入れ、攪拌
翼で15分間混合、攪拌した。攪拌槽の温度は約60℃
に加熱、保持した。次いで、脱塩槽排水と軽油の混合物
をCPIオイルセパレータに送り、静置分離して、水層
と油層を得た。水層の処理済み排水中に含まれる固形分
は5重量ppm、油分は10重量ppm、及びフェノール類は
1重量ppmであり、除去率90%乃至95%であった。
一方、油層に含まれる固形分は500重量ppm、水分は
1重量%であった。
(Example) 100 ppm by weight of a solid having an average particle diameter of 10 μm, 100 ppm by weight of an oil component, and 10% by weight of other organic substances as phenols are contained in a wastewater of a crude oil desalination tank. Light oil was placed in a stirring tank at a ratio of 0.2 part by volume to 1 part by volume of the drainage, and mixed and stirred by a stirring blade for 15 minutes. The temperature of the stirring tank is about 60 ° C
And held. Next, the mixture of the water from the desalination tank and light oil was sent to a CPI oil separator and separated by standing to obtain an aqueous layer and an oil layer. The solid content contained in the treated wastewater of the aqueous layer was 5 ppm by weight, the oil content was 10 ppm by weight, and the phenols were 1 ppm by weight, and the removal rate was 90% to 95%.
On the other hand, the solid content in the oil layer was 500 ppm by weight, and the water content was 1% by weight.

【0013】なお、上記実施例及び後述の比較例におい
て、固形分の測定は、水中に含まれる固形分の場合、1
0μmのフロロポアフィルタで濾過し、フィルタ上に捕
捉された物質を十分な量の80℃の純水、次いで十分な
量の80℃のトルエンで洗浄し、残留物を固形分として
定量した。また、油中に含まれる固形分の場合には、そ
の油を十分な量の80℃のトルエンに溶解し、これを1
0μmのフロロポアフィルタで濾過し、フィルタ上に捕
捉された物質を十分な量の80℃の純水で洗浄し、残留
物を固形分として定量した。
In the above Examples and Comparative Examples described later, the solid content was measured for solids contained in water.
After filtration through a 0 μm fluoropore filter, the substance captured on the filter was washed with a sufficient amount of pure water at 80 ° C. and then with a sufficient amount of toluene at 80 ° C., and the residue was quantified as a solid content. In the case of the solid content contained in the oil, the oil is dissolved in a sufficient amount of toluene at 80 ° C.
The solution was filtered through a 0 μm fluoropore filter, the substance captured on the filter was washed with a sufficient amount of pure water at 80 ° C., and the residue was quantified as a solid content.

【0014】(比較例)上記実施例で用いた脱塩槽排水
を、炭化水素油と混合攪拌することなく、そのままCP
Iオイルセパレータに送り、静置分離した。CPIオイ
ルセパレータの水層出口より採取した処理済排水中の固
形分は、CPIオイルセパレータ投入前の脱塩槽排水と
同じ100重量ppmであり、固形分を除去することがで
きなかった。
(Comparative Example) The wastewater from the desalination tank used in the above example was mixed with hydrocarbon oil without mixing and stirring.
It was sent to an I oil separator and separated by standing. The solid content in the treated waste water collected from the water layer outlet of the CPI oil separator was 100 ppm by weight, which was the same as that in the desalination tank waste water before the CPI oil separator was charged, and the solid content could not be removed.

【0015】[0015]

【発明の効果】本発明の排水の処理方法は、固形分を含
有する排水に炭化水素油を混合した後、静置して水層と
油層に分離するものである。これにより、排水から効率
的に固形分を除去することができ、特に固形分が微粒子
状で安定な状態で分散されている含油排水の処理に有効
である。
According to the wastewater treatment method of the present invention, a hydrocarbon oil is mixed with a wastewater containing a solid content, and the mixture is allowed to stand and separated into an aqueous layer and an oil layer. This makes it possible to efficiently remove solids from the wastewater, and is particularly effective in treating oil-containing wastewater in which the solids are dispersed in a fine and stable state.

フロントページの続き (72)発明者 大橋 満広 愛知県知多市北浜町25番 株式会社ジャパ ンエナジー内 Fターム(参考) 4D037 AA12 AB02 BA11 BB04 BB08 4D051 AA01 BA09 Continued on the front page (72) Inventor Mitsuhiro Ohashi 25th Kitahama-cho, Chita-shi, Aichi Japan Energy Co., Ltd. F-term (reference) 4D037 AA12 AB02 BA11 BB04 BB08 4D051 AA01 BA09

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 固形分を分散状態で含有する排水に炭化
水素油を混合した後、静置により水層と油層に分離する
ことを特徴とする固形分を含有する排水の処理方法。
1. A method for treating wastewater containing solids, comprising mixing hydrocarbon oil with wastewater containing solids in a dispersed state, and separating the mixture into an aqueous layer and an oily layer by standing.
JP32439399A 1999-11-15 1999-11-15 Method for treating waste water containing solid content Withdrawn JP2001137839A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP32439399A JP2001137839A (en) 1999-11-15 1999-11-15 Method for treating waste water containing solid content

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP32439399A JP2001137839A (en) 1999-11-15 1999-11-15 Method for treating waste water containing solid content

Publications (1)

Publication Number Publication Date
JP2001137839A true JP2001137839A (en) 2001-05-22

Family

ID=18165301

Family Applications (1)

Application Number Title Priority Date Filing Date
JP32439399A Withdrawn JP2001137839A (en) 1999-11-15 1999-11-15 Method for treating waste water containing solid content

Country Status (1)

Country Link
JP (1) JP2001137839A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105129894A (en) * 2015-09-09 2015-12-09 江西玛德精细化学工业有限公司 High efficiency extraction method of T-acid mother liquor

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105129894A (en) * 2015-09-09 2015-12-09 江西玛德精细化学工业有限公司 High efficiency extraction method of T-acid mother liquor
CN105129894B (en) * 2015-09-09 2018-03-06 江西玛德精细化学工业有限公司 A kind of T-acid mother liquor Efficient extraction method

Similar Documents

Publication Publication Date Title
US4722781A (en) Desalting process
US2761563A (en) Method of treating water
US6214236B1 (en) Process for breaking an emulsion
CN100395313C (en) Method for removing powder of catalyst from catalytic cracking oil slurry
CN105316018B (en) A kind of coal tar deep processing preprocess method
CN104556595B (en) A kind for the treatment of process of oily sludge
WO2014091498A2 (en) Process for treatment of crude oil, sludges and emulsions
US4350596A (en) Method and apparatus for recovering waste oil
CN104386846A (en) Treatment method and treatment system for oily sewage
CN104291541A (en) Method for recycling crude oil from storage and transportation oil sludge
US4123357A (en) Recovering oil from emulsion by stirring, heating, and settling
CA2719268A1 (en) Microwave process and apparatus for breaking emulsions
EP0291174B1 (en) Process for treatment of contaminated emulsion
CN203333614U (en) Regenerating device for waste emulsified liquid generated in steel rolling process
CN1085193A (en) The method and apparatus of refiltered oil from oily sludge
US2320106A (en) Purification of oil
JP2001137839A (en) Method for treating waste water containing solid content
JPH01275692A (en) Method of treating waste engine oil
CN109536202A (en) A kind of preprocess method of cold-rolling oil Preparation of Biodiesel from Waste Oils raw material
JPH0838942A (en) Method for processing oily suspension
CN113429078A (en) Treatment method of oily wastewater
JP4679680B2 (en) Desalination method for oil containing solids
US5458765A (en) Process of drying and removing solids from waste oil
WO2001074468A2 (en) Processes for separation of oil/water emulsions
JP2017039088A (en) Processing method and processing apparatus of oily waste water

Legal Events

Date Code Title Description
A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A712

Effective date: 20040209

RD03 Notification of appointment of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7423

Effective date: 20040309

A300 Withdrawal of application because of no request for examination

Free format text: JAPANESE INTERMEDIATE CODE: A300

Effective date: 20070206