JP2000350984A - Method and apparatus for treating oil-containing waste water - Google Patents

Method and apparatus for treating oil-containing waste water

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Publication number
JP2000350984A
JP2000350984A JP11164062A JP16406299A JP2000350984A JP 2000350984 A JP2000350984 A JP 2000350984A JP 11164062 A JP11164062 A JP 11164062A JP 16406299 A JP16406299 A JP 16406299A JP 2000350984 A JP2000350984 A JP 2000350984A
Authority
JP
Japan
Prior art keywords
oil
pressurized
petroleum
wastewater
treated water
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.)
Pending
Application number
JP11164062A
Other languages
Japanese (ja)
Inventor
Shigeru Uchiyama
茂 内山
Keiko Katani
圭子 加谷
Sakae Fukunaga
栄 福永
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.)
IHI Corp
Original Assignee
IHI 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 IHI Corp filed Critical IHI Corp
Priority to JP11164062A priority Critical patent/JP2000350984A/en
Publication of JP2000350984A publication Critical patent/JP2000350984A/en
Pending legal-status Critical Current

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  • Apparatus Associated With Microorganisms And Enzymes (AREA)
  • Physical Water Treatments (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently remove an oil component in oil-containing waste water high in concn. up to a concn. possible to discharge. SOLUTION: The greater part of an oil component in oil-containing water high in concn. is removed in a pressure flotation treatment tank 11 to obtain treated water, which is, in turn, allowed to flow to a bioreactor 13 packed with a petroleum adsorbing. material not only to adsorb the oil component by the petroleum adsorbing material 33 but also to decompose the adsorbed oil by petroleum decomposing bacteria.

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、工場等からの含油
廃水の処理方法及びその装置に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for treating oil-containing wastewater from factories and the like.

【0002】[0002]

【従来の技術】従来、工場から切削油を多く含む廃水や
船舶のビルジ廃水等の廃水には、数万〜数十万ppmの
油分が含まれている。
2. Description of the Related Art Conventionally, wastewater containing a large amount of cutting oil from a factory or wastewater such as bilge wastewater of ships contains tens of thousands to hundreds of thousands of ppm of oil.

【0003】この含油廃水の処理は、先ず加圧浮上分離
法により、すなわち、含油廃水中に加圧空気を吹き込
み、その吹き込んだ加圧空気の泡で、油分を浮上させて
廃水から大部分の油分分離除去を行い、次に処理排水中
に数100ppmの濃度で残存する希薄な油分を活性炭
を用いて、数ppm以下まで浄化処理している。
[0003] The treatment of the oil-containing wastewater is carried out first by pressurized flotation, that is, by blowing pressurized air into the oil-containing wastewater, and the foam of the blown compressed air causes the oil to float to remove most of the wastewater from the wastewater. The oil is separated and removed, and then the dilute oil remaining in the treated wastewater at a concentration of several hundred ppm is purified using activated carbon to several ppm or less.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、加圧浮
上分離処理後の処理水中には数100ppmの油分が含
まれることから、これを数10ppm以下まで下げない
と、活性炭にかかる負荷が大きいため、活性炭を再生サ
イクルが短くなり、コスト高となってしまう。
However, since the treated water after the pressurized flotation treatment contains several hundred ppm of oil, the load on the activated carbon is large unless this is reduced to several tens of ppm or less. The cycle for regenerating activated carbon is shortened and the cost is increased.

【0005】このように、通常高濃度の油分分離を目的
とする加圧浮上分離法を適用することは難しく、また活
性炭などの吸着剤を通した場合、油分濃度をできるだけ
下げないと、すぐに油飽和になってしまい、また目詰ま
りなどの問題がある。
[0005] As described above, it is usually difficult to apply the pressure flotation method for the purpose of separating oil at a high concentration, and when passing through an adsorbent such as activated carbon, if the oil concentration is not reduced as much as possible, it will be immediate. Oil saturation occurs, and there are problems such as clogging.

【0006】そこで、活性炭にかかる油分負荷を軽減す
るには、加圧浮上分離装置の下流で、かつ活性炭による
油分除去の前に、数100ppm程度の比較的薄い濃度
の油分を除去する装置を組み込むことが試みられてい
る。
Therefore, in order to reduce the oil load on the activated carbon, a device for removing an oil having a relatively low concentration of about several hundred ppm is incorporated downstream of the pressurized flotation device and before the oil is removed by the activated carbon. Have been tried.

【0007】この加圧浮上分離処理で、数100ppm
までに希薄になった含油分の除去を行う場合、油分は、
排水中に含まれている界面活性剤により水面に浮上せ
ず、水中に溶け込んだ形で存在するため、中空糸膜等の
膜分離装置で油分を分離することも考えれれるが、圧力
をかけて分離するためランニングコストが高くなる問題
がある。
[0007] In this pressure flotation treatment, several hundred ppm
When removing the oil content that has become diluted by
Since the surfactant contained in the wastewater does not float on the water surface and exists in a form dissolved in the water, it is conceivable to separate oil using a membrane separation device such as a hollow fiber membrane. There is a problem that running costs increase due to separation.

【0008】そこで、本発明の目的は、上記課題を解決
し、高濃度の含油廃水中の油分を放流できる濃度まで効
率よく除去できる含油廃水処理方法及びその装置を提供
することにある。
Accordingly, an object of the present invention is to solve the above-mentioned problems and to provide an oil-containing wastewater treatment method and an apparatus thereof that can efficiently remove oil components in high-concentration oil-containing wastewater to a concentration that can be discharged.

【0009】[0009]

【課題を解決するための手段】上記目的を達成するため
に、請求項1の発明は、高濃度の含油廃水を加圧浮上処
理にてその排水中の油分の大部分を除去し、その処理水
を石油吸着材を充填したバイオリアクタに流し、その石
油吸着材に油分を吸着させると共に石油分解細菌で、そ
の吸着した油分を分解させる含油廃水処理方法である。
In order to achieve the above object, an invention according to claim 1 is to remove most of the oil content in high-concentration oil-containing wastewater by pressurized floating treatment. This is an oil-containing wastewater treatment method in which water is flowed into a bioreactor filled with a petroleum adsorbent to adsorb oil to the petroleum adsorbent and decompose the adsorbed oil by petroleum-degrading bacteria.

【0010】請求項2の発明は、高濃度の含油廃水と加
圧空気とを加圧タンク内で混合させた後、加圧浮上処理
する請求項1記載の含油廃水処理方法である。
The second aspect of the present invention is the method for treating oil-impregnated wastewater according to claim 1, wherein high-concentration oil-impregnated wastewater and pressurized air are mixed in a pressurized tank and then subjected to pressure flotation treatment.

【0011】請求項3の発明は、高濃度の含油廃水中の
油分を加圧空気で浮上分離させる加圧浮上処理槽と、加
圧浮上処理槽の処理水を連続的に導入し、石油吸着材が
充填され、その石油吸着材に吸着された油分を石油分解
細菌で分解するバイオリアクタとを備えた含油廃水処理
装置である。
According to a third aspect of the present invention, a pressurized flotation tank for levitation and separation of oil in high-concentration oil-containing wastewater with pressurized air, and treated water in the pressurized flotation tank are continuously introduced to adsorb oil. An oil-containing wastewater treatment apparatus comprising a bioreactor filled with a material and decomposing oil adsorbed on the petroleum adsorbent with petroleum-degrading bacteria.

【0012】請求項4の発明は、加圧浮上処理槽に、含
油廃水と加圧空気を予混合する加圧タンクを接続した請
求項3記載の含油廃水処理装置である。
According to a fourth aspect of the present invention, there is provided the oil-impregnated wastewater treatment apparatus according to the third aspect, wherein a pressurized tank for premixing the oil-impregnated wastewater and the pressurized air is connected to the pressurized floating treatment tank.

【0013】[0013]

【発明の実施の形態】以下、本発明の好適一実施の形態
を添付図面に基づいて詳述する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A preferred embodiment of the present invention will be described below in detail with reference to the accompanying drawings.

【0014】図1は、本発明の含油廃水処理のフローを
示したものである。
FIG. 1 shows the flow of the oil-containing wastewater treatment of the present invention.

【0015】本発明の含油廃水処理装置は、高濃度の含
油廃水と加圧空気を混合する加圧タンク10と、その加
圧タンク10からの含油廃水と加圧空気を導入し、廃水
中の油分を浮上分離させる加圧浮上処理槽11と、加圧
浮上処理槽11の処理水を連続的に導入し、充填された
石油吸着材12で油分を吸着すると共に石油分解細菌で
油分を分解するバイオリアクタ13と、そのバイオリア
クタ13からの処理水中に含まれる油分を吸着して放流
するための後処理装置14とからなっている。また、加
圧浮上処理槽11には浮上分離された油分等を貯留する
スカム貯槽15が接続される。
The oil-impregnated wastewater treatment apparatus of the present invention comprises a pressurized tank 10 for mixing high-concentration oil-impregnated wastewater and pressurized air, and introducing the oil-impregnated wastewater and pressurized air from the pressurized tank 10 into the wastewater. A pressurized flotation tank 11 for separating and floating oil, and treated water in the pressurized flotation tank 11 are continuously introduced, the oil is adsorbed by the filled oil adsorbent 12, and the oil is decomposed by petroleum-degrading bacteria. The bioreactor includes a bioreactor 13 and a post-treatment device 14 for adsorbing and discharging oil contained in the treated water from the bioreactor 13. In addition, a scum storage tank 15 for storing the oil separated by flotation is connected to the pressurized flotation tank 11.

【0016】以下これをさらに詳しく説明する。Hereinafter, this will be described in more detail.

【0017】加圧タンク10には、数万〜数十万ppm
の油分が含まれた高濃度の含油廃水を昇圧する昇圧ポン
プ16と開閉弁17が接続された含油廃水供給ライン1
8が接続されると共に、コンプレッサ19と開閉弁20
が接続された加圧空気供給ライン21とが接続される。
In the pressurized tank 10, tens of thousands to hundreds of thousands ppm
Oil-impregnated wastewater supply line 1 in which a booster pump 16 for increasing the pressure of high-concentration oil-impregnated wastewater containing oil and an on-off valve 17 are connected
8 is connected, and the compressor 19 and the on-off valve 20
Is connected to the pressurized air supply line 21 to which is connected.

【0018】加圧タンク10で、予混合された含油廃水
と加圧空気は、開閉弁22より供給ライン23にて、加
圧浮上処理槽11に供給される。
The oil-containing wastewater and pressurized air premixed in the pressurized tank 10 are supplied to the pressurized floating treatment tank 11 through a supply line 23 through an on-off valve 22.

【0019】加圧浮上処理槽11は、セパレータ24に
て浮上分離室25と処理水回収室26とに分離される。
このセパレータ24は、上下に加圧浮上処理槽11の上
下壁と間隙を形成するように形成され、上部の間隙で、
浮上分離室25と処理水回収室26の空間を連通し、下
部の間隙で、浮上分離室25の処理液を処理水回収室2
6に流すようになっており、また加圧浮上処理槽11の
頂部にはベンチュリー管27が設けられる。
The pressurized flotation tank 11 is separated by a separator 24 into a flotation separation chamber 25 and a treated water recovery chamber 26.
The separator 24 is formed so as to form a gap with the upper and lower walls of the pressurized flotation tank 11 vertically.
The space between the flotation separation chamber 25 and the treated water recovery chamber 26 is communicated, and the processing liquid in the flotation separation chamber 25 is supplied to the treated water recovery chamber 2 through a gap below.
6 and a venturi tube 27 is provided at the top of the pressurized flotation tank 11.

【0020】浮上分離室25の下部に供給ライン23の
吹込口23aが設けられると共に上部に浮上分離した油
分を回収するオーバーフロー管28が設けられ、そのオ
ーバーフロー管28の下方に開閉弁29を介してスカム
貯槽15が接続される。
An inlet 23a of the supply line 23 is provided at the lower part of the floating separation chamber 25, and an overflow pipe 28 for recovering the oil separated by floating is provided at the upper part. An opening / closing valve 29 is provided below the overflow pipe 28 through an on-off valve 29. The scum storage tank 15 is connected.

【0021】処理水回収室26には、オーバーフロー管
28の位置に合わせて排水口30が設けられ、その排水
口30に処理水ライン31を介してバイオリアクタ13
が接続される。
A drain port 30 is provided in the treated water recovery chamber 26 in accordance with the position of the overflow pipe 28, and the drain port 30 is connected to the bioreactor 13 via a treated water line 31.
Is connected.

【0022】バイオリアクタ13は、容器32内に合成
繊維等からなる石油吸着材33が充填された充填層34
が設けられ、その容器32の上部に処理水ライン31が
接続され、下部に分解処理後の処理水の排水ライン35
が接続されると共に容器32の底部より空気を吹き込む
べくブロワ36、開閉弁37が接続された空気ライン3
8が接続される。
The bioreactor 13 includes a packed bed 34 in which a petroleum adsorbent 33 made of a synthetic fiber or the like is filled in a container 32.
The treated water line 31 is connected to the upper part of the container 32, and the treated water drain line 35 after the decomposition treatment is
And an air line 3 to which a blower 36 and an on-off valve 37 are connected to blow air from the bottom of the container 32.
8 is connected.

【0023】排水ライン35には、開閉弁39を介して
活性炭などが充填された後処理装置14が接続され、そ
の後処理装置14に排水弁40を介して放流ライン41
が接続される。
The drainage line 35 is connected to a post-processing device 14 filled with activated carbon or the like via an on-off valve 39, and then the discharge line 41 is connected to the processing device 14 via a drainage valve 40.
Is connected.

【0024】この排水ライン35は、開閉弁39から上
方に立ち上げた立上ライン35aにT字継手45が接続
され、そのT字継手45に、上方に延びる大気導入ライ
ン46が接続されると共に水平に延びると共に下方に曲
げられた排出ライン35bが接続され、その排出ライン
35bに後処理装置14が接続される。またバイオリア
クタ13の容器32頂部には、ベンチュリー管47が設
けられる。
In the drain line 35, a T-shaped joint 45 is connected to a rising line 35a rising upward from an on-off valve 39, and an air introduction line 46 extending upward is connected to the T-shaped joint 45. A discharge line 35b extending horizontally and bent downward is connected, and the post-processing device 14 is connected to the discharge line 35b. A Venturi tube 47 is provided on the top of the container 32 of the bioreactor 13.

【0025】このように、排水ライン35を立ち上げて
た後、T字継手45にて水平にしたのち立ち下げ、T字
継手45に大気導入ライン46を接続すると共に容器3
2頂部にベンチュリー管47を設けることで、バイオリ
アクタ13内の処理水の液面は、T字継手45の位置に
保たれるようになっている。
As described above, after the drainage line 35 has been raised, the drainage line 35 is leveled by the T-shaped joint 45 and then lowered.
By providing the venturi tube 47 at the top of the two, the liquid level of the treated water in the bioreactor 13 is maintained at the position of the T-shaped joint 45.

【0026】なお、42は、加圧タンク10に接続した
排出弁、43はスカム貯槽15内に溜まった油分を排出
する廃油ライン、44はそのライン43に接続した弁で
ある。
Reference numeral 42 denotes a discharge valve connected to the pressurized tank 10, reference numeral 43 denotes a waste oil line for discharging oil accumulated in the scum storage tank 15, and reference numeral 44 denotes a valve connected to the line 43.

【0027】以上において、数万〜数十万ppmの濃度
の含油廃水が昇圧ポンプ16により含油廃水供給ライン
18から加圧タンク10内に供給され、同時にコンプレ
ッサ19から加圧供給ライン21を介して加圧空気が加
圧タンク10内に供給され、加圧タンク10内で含油廃
水と加圧空気が予混合された後、供給ライン23の吹込
口23aから加圧浮上処理槽11の浮上分離室25の処
理水中に吹き込まれる。
In the above, oil-containing wastewater having a concentration of tens of thousands to hundreds of thousands of ppm is supplied from the oil-containing wastewater supply line 18 into the pressurized tank 10 by the booster pump 16 and simultaneously from the compressor 19 via the pressurized supply line 21. After the pressurized air is supplied into the pressurized tank 10 and the oil-containing wastewater and the pressurized air are premixed in the pressurized tank 10, the flotation separation chamber of the pressurized flotation tank 11 is supplied from the inlet 23 a of the supply line 23. It is blown into 25 treated waters.

【0028】この吹き込みにより、加圧空気は泡となっ
て処理水内を上昇すると共に処理水中に含まれる油分も
泡とともに上昇させて含油廃水中の油分の大部分が泡で
浮上分離される。
Due to this blowing, the pressurized air rises in the treated water as bubbles, and the oil contained in the treated water also rises with the bubbles, so that most of the oil in the oil-containing wastewater is floated and separated by the bubbles.

【0029】この際、加圧タンク10内で含油廃水と加
圧空気と予混合して浮上分離室25の処理水中に吹き込
むことで、油分と空気とが混ざり合うと共に加圧空気の
膨張でより細かい空気の泡となると共に油分を効率よく
捕捉して処理水から分離浮上させることができる。
At this time, the oil-containing wastewater and the pressurized air are premixed in the pressurized tank 10 and blown into the treated water in the flotation chamber 25, so that the oil and the air are mixed and the compressed air expands. It becomes fine air bubbles and efficiently captures oil and separates and floats from the treated water.

【0030】処理水から浮上した油分はオーバーフロー
管28よりスカム貯槽15に流下し、適宜廃油ライン4
3より排出されて産業廃棄物として処理される。
The oil floating from the treated water flows down from the overflow pipe 28 to the scum storage tank 15 and is appropriately drained from the waste oil line 4.
3 to be disposed of as industrial waste.

【0031】加圧浮上処理槽11の浮上分離室25では
大部分の油分が分離除去できるが数100ppmの油分
が処理水に残り、これを処理水回収室26から処理水ラ
イン31を介してバイオリアクタ13に供給する。
Most of the oil content can be separated and removed in the flotation separation chamber 25 of the pressurized flotation treatment tank 11, but several hundred ppm of oil remains in the treated water, which is transferred from the treated water recovery chamber 26 to the treated water line 31 via the treated water line 31. It is supplied to the reactor 13.

【0032】バイオリアクタ13内には、石油吸着材3
3が充填されており、処理水中の油分は、その石油吸着
材33に吸着され、石油分解細菌によりその吸着された
油分が分解される。
In the bioreactor 13, the oil adsorbent 3
3, the oil in the treated water is adsorbed by the petroleum adsorbent 33, and the adsorbed oil is decomposed by petroleum-degrading bacteria.

【0033】図2は、石油吸着材33と処理水中の油分
が吸着されて石油分解細菌で分解除去される状態を模式
的に示したものである。
FIG. 2 schematically shows a state in which an oil component in the petroleum adsorbent 33 and the treated water is adsorbed and decomposed and removed by petroleum degrading bacteria.

【0034】先ず、図2(a)に示すように石油吸着材
33に処理水を連続的に流すと、図2(b)に示すよう
に、石油吸着材33に処理水中の油oが付着乃至吸着さ
れる。
First, as shown in FIG. 2 (a), when treated water is continuously passed through the oil adsorbent 33, the oil o in the treated water adheres to the oil adsorbent 33 as shown in FIG. 2 (b). Or adsorbed.

【0035】この石油吸着材33に吸着された油oは、
図2(c)に示すように石油吸着材33に固定された石
油分解細菌pにより、図2(d)に示すように石油吸着
材33に吸着された油oを資化する石油分解細菌pが増
殖しつつその油oを分解する。
The oil o adsorbed by the oil adsorbent 33 is
As shown in FIG. 2C, the petroleum-degrading bacteria p immobilized on the oil adsorbent 33 as shown in FIG. Decomposes the oil o while growing.

【0036】この石油分解細菌pによる油の分解は、長
鎖構造の石油分子を、先ず短鎖構造の石油分子に分解
し、これを有機酸・脂肪酸に分解すると共に更にこれを
分解して水と二酸化炭素にまで分解しつつ石油分解細菌
pが増殖していく。
The oil is decomposed by the petroleum-degrading bacteria p. First, petroleum molecules having a long-chain structure are decomposed into petroleum molecules having a short-chain structure, which are further decomposed into organic acids and fatty acids, and further decomposed into water. The petroleum-degrading bacteria p grow while decomposing to carbon dioxide.

【0037】この石油分解細菌pは、活性汚泥中に通常
に含まれる細菌であり、石油吸着材33に油を吸着させ
た後、活性汚泥を添加して石油分解細菌pを増殖させ固
定させる。また石油分解細菌pの増殖は好気性雰囲気に
保つ必要があるため、空気ライン38から空気をバイオ
リアクタ13内に吹き込んでおく。
This petroleum-degrading bacterium p is a bacterium normally contained in activated sludge. After oil is adsorbed on the petroleum adsorbent 33, activated sludge is added to propagate and fix the petroleum-degrading bacterium p. Since the growth of the petroleum-degrading bacteria p needs to be maintained in an aerobic atmosphere, air is blown into the bioreactor 13 from the air line 38.

【0038】通常、石油吸着材33による油の吸着は処
理水を連続的に流すと、一定時間後には吸着できる油は
飽和状態になり、それ以上油を吸着できなくなるが、石
油吸着材33に固定された石油分解細菌で分解すること
で吸着能力が常に一定に保たれ、処理水中の油分を吸着
しつつ石油分解細菌の作用により効率的に油が分解され
るようになる。
Normally, the oil is adsorbed by the oil adsorbent 33 when the treated water is continuously flowed, and after a certain period of time, the oil that can be adsorbed becomes saturated and the oil can no longer be adsorbed. By decomposing with the fixed petroleum-degrading bacteria, the adsorption capacity is always kept constant, and the oil is efficiently decomposed by the action of the petroleum-degrading bacteria while adsorbing the oil component in the treated water.

【0039】この場合、高濃度の含油廃水をそのままバ
イオリアクタ13に流すと、油分の吸着能と石油分解細
菌による分解能がマッチングせず石油吸着材による油吸
着が飽和状態となり目詰まりを起こすが、前段の加圧浮
上処理槽11で油分濃度を数100ppmまで落とすこ
とで、吸着能と石油分解細菌による分解能がマッチング
が良好となる。
In this case, if the high-concentration oil-containing wastewater is passed directly to the bioreactor 13, the oil adsorption capacity and the resolution by the petroleum-decomposing bacteria do not match, and the oil adsorption by the oil adsorbent becomes saturated, causing clogging. By reducing the oil concentration to several hundred ppm in the pressure flotation tank 11 in the former stage, the matching between the adsorption capacity and the resolution by the petroleum-degrading bacteria becomes good.

【0040】バイオリアクタ13による分解処理後の油
分濃度は数10ppmとなり、この処理水を排水ライン
35から活性炭などが充填された後処理装置14に流し
て油分を吸着除去して放流ライン41から油分濃度数p
pmの廃水として放流する。
The oil concentration after the decomposition treatment by the bioreactor 13 is several tens of ppm. The treated water is passed from the drain line 35 to the post-treatment device 14 filled with activated carbon or the like to adsorb and remove the oil component, and is discharged from the discharge line 41 to the oil component. Concentration number p
Discharge as pm wastewater.

【0041】このように後処理装置14には、数10p
pmの油分濃度の処理水が供給されるため、活性炭など
の再生のサイクルは長くなり効率の良いものとなる。
As described above, the post-processing device 14 has several tens of
Since the treated water having an oil concentration of pm is supplied, the cycle of regeneration of activated carbon or the like becomes longer and the efficiency becomes higher.

【0042】図3は、バイオリアクタによる油分解能の
経日変化のデータを示したもので、aは、バイオリアク
タに流入させた処理水の油濃度の経日変化を、bは本発
明の石油吸着材に石油分解菌を固定させて処理した処理
後の処理水の油濃度の経日変化を、cは比較としてバイ
オリアクタ内に石油吸着材を充填せずに活性汚泥を滞留
させたときの処理後の処理水の油濃度の経日変化を示し
ている。
FIG. 3 shows data on the daily change of the oil resolution by the bioreactor, wherein a shows the daily change of the oil concentration of the treated water flowing into the bioreactor, and b shows the oil concentration of the present invention. The daily change in the oil concentration of the treated water after treatment with the petroleum degrading bacteria immobilized on the adsorbent, and c is a comparison when the activated sludge is retained without filling the petroleum adsorbent in the bioreactor. 5 shows the daily change of the oil concentration of the treated water after the treatment.

【0043】この場合、油濃度はn−ヘキサン抽出物質
濃度(mg/L=ppm)で求めた。
In this case, the oil concentration was determined by the concentration of the n-hexane extract (mg / L = ppm).

【0044】図3より、加圧浮上処理槽で処理され、バ
イオリアクタ13に流入する流入処理水の油分濃度は、
300〜500ppmであるが、本発明のバイオリアク
タで処理した場合、bに示すように約30ppmの濃度
にできる。これに対してcに示すように比較例では約1
00ppmの濃度までしか油を分解できない。
As shown in FIG. 3, the oil concentration of the inflowing treated water treated in the pressurized flotation treatment tank and flowing into the bioreactor 13 is as follows:
It is 300 to 500 ppm, but when treated with the bioreactor of the present invention, a concentration of about 30 ppm can be obtained as shown in b. On the other hand, as shown in FIG.
It can only degrade oil up to a concentration of 00 ppm.

【0045】[0045]

【発明の効果】以上要するに本発明によれば、加圧浮上
分離後の数100ppmの油分濃度の処理水を石油吸着
材を充填したバイオリアクタに連続的に流すことによっ
て、石油吸着材に油を吸着させ、その吸着した油を資化
する石油分解細菌によって分解させつつ石油分解細菌を
増殖させることで、その後、活性炭等により吸着して放
流処理する際の負荷を軽減できると共に保守・管理が容
易になる。
In summary, according to the present invention, the treated water having an oil concentration of several hundred ppm after pressure flotation is continuously passed through the bioreactor filled with the petroleum adsorbent, whereby the oil is adsorbed on the petroleum adsorbent. By adsorbing and decomposing the adsorbed oil by assimilating petroleum-degrading bacteria and growing the petroleum-degrading bacteria, it is possible to reduce the load when subsequently adsorbing with activated carbon, etc. and release the wastewater, and it is easy to maintain and manage become.

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

【図1】本発明の一実施の形態を示す概略図である。FIG. 1 is a schematic diagram showing an embodiment of the present invention.

【図2】本発明における石油吸着材による油分の吸着と
石油分解菌による分解を説明する模式図である。
FIG. 2 is a schematic view illustrating oil adsorption by a petroleum adsorbent and decomposition by petroleum-decomposing bacteria in the present invention.

【図3】本発明においたバイオリアクタに処理水中の油
分分解の実験データを示す図である。
FIG. 3 is a view showing experimental data of oil decomposition in treated water in the bioreactor according to the present invention.

【符号の説明】[Explanation of symbols]

11 加圧浮上処理槽 13 バイオリアクタ 33 石油吸着材 11 Pressure flotation tank 13 Bioreactor 33 Petroleum adsorbent

───────────────────────────────────────────────────── フロントページの続き (72)発明者 福永 栄 神奈川県横浜市磯子区新中原町1番地 石 川島播磨重工業株式会社機械・プラント開 発センター内 Fターム(参考) 4B029 AA02 BB01 CC02 CC03 CC13 DA06 DB11 DF09 DG06 4D024 AA04 AB06 BA17 BB03 BC01 CA01 DB03 DB08 DB15 4D037 AA11 AB06 BA03 CA01 CA07 4D040 BB42 BB82 DD01 DD31  ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Sakae Fukunaga 1 Shin-Nakahara-cho, Isogo-ku, Yokohama-shi, Kanagawa Ishikawashima-Harima Heavy Industries, Ltd. Machinery and Plant Development Center F term (reference) 4B029 AA02 BB01 CC02 CC03 CC13 DA06 DB11 DF09 DG06 4D024 AA04 AB06 BA17 BB03 BC01 CA01 DB03 DB08 DB15 4D037 AA11 AB06 BA03 CA01 CA07 4D040 BB42 BB82 DD01 DD31

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 高濃度の含油廃水を加圧浮上処理にてそ
の排水中の油分の大部分を除去し、その処理水を石油吸
着材を充填したバイオリアクタに流し、その石油吸着材
に油分を吸着させると共に石油分解細菌で、その吸着し
た油分を分解させることを特徴とする含油廃水処理方
法。
1. A high-concentration oil-containing wastewater is subjected to pressure flotation to remove most of the oil content from the wastewater, and the treated water is passed through a bioreactor filled with an oil adsorbent, and the oil adsorbent is added to the oil adsorbent. A method for treating oil-containing wastewater, comprising adsorbing oil and decomposing the adsorbed oil with petroleum-degrading bacteria.
【請求項2】 高濃度の含油廃水と加圧空気とを加圧タ
ンク内で混合させた後、加圧浮上処理する請求項1記載
の含油廃水処理方法。
2. The oil-impregnated wastewater treatment method according to claim 1, wherein a high-concentration oil-impregnated wastewater and pressurized air are mixed in a pressurized tank and then subjected to a pressurized floating treatment.
【請求項3】 高濃度の含油廃水中の油分を加圧空気で
浮上分離させる加圧浮上処理槽と、加圧浮上処理槽の処
理水を連続的に導入し、石油吸着材が充填され、その石
油吸着材に吸着された油分を石油分解細菌で分解するバ
イオリアクタとを備えたことを特徴とする含油廃水処理
装置。
3. A pressurized flotation tank for levitation and separation of oil in high-concentration oil-containing wastewater with pressurized air, and treated water in the pressurized flotation tank are continuously introduced and filled with an oil adsorbent, An oil-containing wastewater treatment apparatus, comprising: a bioreactor for decomposing oil adsorbed on the petroleum adsorbent with petroleum-degrading bacteria.
【請求項4】 加圧浮上処理槽に、含油廃水と加圧空気
を予混合する加圧タンクを接続した請求項3記載の含油
廃水処理装置。
4. The oil-impregnated wastewater treatment apparatus according to claim 3, wherein a pressurized tank for premixing the oil-impregnated wastewater and pressurized air is connected to the pressurized floating treatment tank.
JP11164062A 1999-06-10 1999-06-10 Method and apparatus for treating oil-containing waste water Pending JP2000350984A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11164062A JP2000350984A (en) 1999-06-10 1999-06-10 Method and apparatus for treating oil-containing waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11164062A JP2000350984A (en) 1999-06-10 1999-06-10 Method and apparatus for treating oil-containing waste water

Publications (1)

Publication Number Publication Date
JP2000350984A true JP2000350984A (en) 2000-12-19

Family

ID=15786067

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11164062A Pending JP2000350984A (en) 1999-06-10 1999-06-10 Method and apparatus for treating oil-containing waste water

Country Status (1)

Country Link
JP (1) JP2000350984A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006346560A (en) * 2005-06-15 2006-12-28 Tottori Univ Method and apparatus for treating oil-containing wastewater, and additive
JP2008173572A (en) * 2007-01-19 2008-07-31 Nishimatsu Constr Co Ltd Turbid water treatment method
JP2009018222A (en) * 2007-07-10 2009-01-29 Sharp Corp Separation column and suspended matter separator
JP2011056332A (en) * 2009-09-07 2011-03-24 Hitachi Industrial Equipment Systems Co Ltd Oil/water separator
KR101096864B1 (en) 2009-03-25 2011-12-22 신우리 The oil separator
CN103214123A (en) * 2013-05-13 2013-07-24 中国地质大学(北京) Integrated coagulation-synergism inclined plate oil-removing device

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006346560A (en) * 2005-06-15 2006-12-28 Tottori Univ Method and apparatus for treating oil-containing wastewater, and additive
JP2008173572A (en) * 2007-01-19 2008-07-31 Nishimatsu Constr Co Ltd Turbid water treatment method
JP2009018222A (en) * 2007-07-10 2009-01-29 Sharp Corp Separation column and suspended matter separator
KR101096864B1 (en) 2009-03-25 2011-12-22 신우리 The oil separator
JP2011056332A (en) * 2009-09-07 2011-03-24 Hitachi Industrial Equipment Systems Co Ltd Oil/water separator
CN103214123A (en) * 2013-05-13 2013-07-24 中国地质大学(北京) Integrated coagulation-synergism inclined plate oil-removing device

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