CN101113031A - Method for treating oil field wastewater by electro-float process - Google Patents
Method for treating oil field wastewater by electro-float process Download PDFInfo
- Publication number
- CN101113031A CN101113031A CNA2006100294509A CN200610029450A CN101113031A CN 101113031 A CN101113031 A CN 101113031A CN A2006100294509 A CNA2006100294509 A CN A2006100294509A CN 200610029450 A CN200610029450 A CN 200610029450A CN 101113031 A CN101113031 A CN 101113031A
- Authority
- CN
- China
- Prior art keywords
- oil
- oil field
- electro
- water
- waste 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
Links
Abstract
The invention relates to wastewater treatment technique field. The electro-floatation method of the invention for the treatment of oil field waste water comprises the steps: a. the oil field waste water comes into a pretreatment area of an electro-floatation device with a scale of 200 - 500 m3/d, and goes through a baffle, comes into an inclined plate precipitation area, to dramatically cut down the oil content in waste water; b. the waste water being pretreated in the pretreatment area of step (a) continuously comes into the electro-floatation area provided with electrode plates to be treated, and the treating condition is: delaying time 5- 30min, current intensity 6000- 15000 A, voltage 3.5 V, and qualified treated water can be acquired.
Description
Technical field
The present invention relates to a kind of wastewater treatment technique field.
Background technology
In oil-field development, oil field later stage particularly, the oil field will produce a large amount of recovered waters, for many years, the technology pattern of a mouthful oil removing section (oil removing ten secondary oil removings) ten fillter sections is mainly adopted in domestic oil field to produced water disposal, wherein " oil removing section " adopts following method substantially: (1) physics method is primarily aimed at the oil slick in the former water: (2) chemical method mainly solves the mark oil in the former water; (3) coarse method is primarily aimed at the dispersed oil in the former water; (4) the stream partition method is mainly removed the oil slick in the former water; (5) the quick air soluble method of air supporting, revulsion are mainly removed oil slick and dispersed oil in the former water.
Aforesaid method is obtained certain effect to the processing of the recovered water in each oil field, and is still along with the raising of injection water quality standard, more and more higher to the requirement of " oil removing section ".The many weak points that exposed in the various treatment processs can not adapt to on-the-spot requirement.Fall as, the physics method only can be removed oil slick and the macrobead suspended substance in the former water, still need increase the secondary oil removal plant: chemical method can only solve dispersed oil and the small granular suspended matters in the former water, oil removal plant of front end is had relatively high expectations, the factor that restricts the normal operation that adds pharmacy work simultaneously is more, is difficult to meet design requirement; The coarse method, higher to the import water quality requirement, treatment effect is difficult to satisfy follow-up filtration unit requirement; The effect of cyclonic separation method removal suspended substance is relatively poor; Air supporting method (induce flotation, spray flotation), mechanical part is many, and energy consumption is higher, less stable, maintenance capacity is big.
In addition, practice explanation for many years, it is whether normal that medicament adds work is one of important factor of determining the produced water disposal effect, also is the lower where the shoe pinches of the long-term water quality reaching standard rate in each oil field.All need add various chemical medicaments in each Oilfield using water technology at present, and at the scene in the actual mechanical process, be that screening, the dosage of medicament, the control that adds point, dosing method, cost, on-the-spot each link such as preparation all may influence treatment effect, make the water quality can not be up to standard.
Summary of the invention
The objective of the invention is to overcome the shortcoming of prior art, propose a kind of method for the treatment of oil field wastewater by electro-float process.
The method for the treatment of oil field wastewater by electro-float process of the present invention may further comprise the steps:
A. the oil field waste scale of entering is the electric floating device pretreating zone of 200-500m3/d, by plate washer, enters the sloping plate deposition district, to reduce the waste water oleaginousness significantly;
B. the waste water after step a pretreating zone is handled enters the electric floating region processing that is provided with battery lead plate continuously, and its treatment condition are: residence time 5-30min, strength of current 6000-15000A, voltage 3.5V obtain the qualified oil field extracted water of water quality at last.
Beneficial effect of the present invention: method of the present invention can realize that electric floating oil removing and electrolytic sterilizing are integrated, and oil removal rate is greater than 90%, and the degerming rate is greater than 99%.According to the pneumatically supported principle of electricity: electric floating in the hydrogen gas bubbles diameter be generally 10-30pm, bubble diameter such as oxygen, chlorine is 20-60um, microbubble has very high specific surface area, tiny oil droplets and suspended substance in can planar water, arrive several thousandths because the density of microbubble only be the hundreds of of the density of water, be easy to oil droplet and suspended substance be isolated water body and remove; Multiple strong oxidizing property materials such as anode produces oxygen, chlorine have stronger germicidal action, and chlorination is not realized the sterilization purpose.In oil field extracted water, on average at 4000.10 ten thousand m/l, specific conductivity is bigger for salinity, uses electricly can regulate the relation that the pole piece spacing changes voltage and current density when floating, needn't add medicament again and regulate specific conductivity, has certain advantage during use; Use electric float method can remove suspended substance and oil slick, dispersed oil effectively, use flocculation agent or add flotation agent, can also remove dispersed oil and be partly dissolved oil: owing to contain a large amount of chlorions in the recovered water, thereby, discharge a large amount of chlorine at electrode and reach the sterilization purpose, therefore, the present invention can guarantee under the effluent quality prerequisite up to standard, solved " bottleneck " problem that each oil-field water of the restriction whole nation is handled, when realizing to add various medicaments in the wastewater treatment process, reduce processing cost significantly, simplified requirement execute-in-place.
Embodiment
Further describe the present invention by the following examples.
Oil field extracted water with oleaginousness 53.90mg/L is tested, oil field waste specifically flows to: oil field waste at first enters the cloth pool by water inlet pipe, climb over baffle plate then, enter swash plate, make oily(waste)water at the swash plate sharp separation, most of oil slick floats to the oil-collecting bag, other dispersed oil and part oil slick water flow through the voltage stabilizing district and enter electric floating region, its operational condition: unit scale Q=200500m3/d, residence time 5-30rain, strength of current 5 (X) 0---15000A, voltage 3-5V, produce a large amount of micro bubbles at electrode, oil slick in the sewage, most of dispersed oil and part oil in water emulsion fat vacuole come-up, sticking float on the micro bubble and brought to the water surface, oil slick enters the oil-collecting bag, and the sewage after the processing is taken device by effluent trough or pipe out of by rising pipe.Display effect is fine as a result, and the water quality of coming out at last is qualified.
Claims (1)
1. the method for the treatment of oil field wastewater by electro-float process of the present invention may further comprise the steps:
A. the oil field waste scale of entering is the electric floating device pretreating zone of 200-500m3/d, by plate washer, enters the sloping plate deposition district, to reduce the waste water oleaginousness significantly;
B. the waste water after step a pretreating zone is handled enters the electric floating region processing that is provided with battery lead plate continuously, and its treatment condition are: residence time 5-30min, strength of current 6000-15000A, voltage 3.5V obtain the qualified oil field extracted water of water quality at last.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNA2006100294509A CN101113031A (en) | 2006-07-27 | 2006-07-27 | Method for treating oil field wastewater by electro-float process |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNA2006100294509A CN101113031A (en) | 2006-07-27 | 2006-07-27 | Method for treating oil field wastewater by electro-float process |
Publications (1)
Publication Number | Publication Date |
---|---|
CN101113031A true CN101113031A (en) | 2008-01-30 |
Family
ID=39021589
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNA2006100294509A Pending CN101113031A (en) | 2006-07-27 | 2006-07-27 | Method for treating oil field wastewater by electro-float process |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN101113031A (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105000727A (en) * | 2015-09-02 | 2015-10-28 | 波鹰(厦门)科技有限公司 | Oil-field wastewater treating and recycling device |
CN105130069A (en) * | 2015-09-02 | 2015-12-09 | 波鹰(厦门)科技有限公司 | High-salt oil producing waste water treatment and recycling device |
CN107226578A (en) * | 2016-03-24 | 2017-10-03 | 长江三星能源科技股份有限公司 | One kind is used for offshore oilfield polymer-bearing waste-water reinjection treatment method |
CN107235617A (en) * | 2017-05-16 | 2017-10-10 | 方明环保科技(漳州)有限公司 | Oil gas field oil-cut mud landwaste processing method and equipment |
CN107235618A (en) * | 2017-05-16 | 2017-10-10 | 方明环保科技(漳州)有限公司 | Sludge in Oilfields recycling processing method and equipment |
CN113830943A (en) * | 2021-10-08 | 2021-12-24 | 江苏京源环保股份有限公司 | Ultrasonic-combined efficient electric floating sewage treatment process and treatment equipment thereof |
-
2006
- 2006-07-27 CN CNA2006100294509A patent/CN101113031A/en active Pending
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105000727A (en) * | 2015-09-02 | 2015-10-28 | 波鹰(厦门)科技有限公司 | Oil-field wastewater treating and recycling device |
CN105130069A (en) * | 2015-09-02 | 2015-12-09 | 波鹰(厦门)科技有限公司 | High-salt oil producing waste water treatment and recycling device |
CN107226578A (en) * | 2016-03-24 | 2017-10-03 | 长江三星能源科技股份有限公司 | One kind is used for offshore oilfield polymer-bearing waste-water reinjection treatment method |
CN107235617A (en) * | 2017-05-16 | 2017-10-10 | 方明环保科技(漳州)有限公司 | Oil gas field oil-cut mud landwaste processing method and equipment |
CN107235618A (en) * | 2017-05-16 | 2017-10-10 | 方明环保科技(漳州)有限公司 | Sludge in Oilfields recycling processing method and equipment |
CN113830943A (en) * | 2021-10-08 | 2021-12-24 | 江苏京源环保股份有限公司 | Ultrasonic-combined efficient electric floating sewage treatment process and treatment equipment thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102936072B (en) | Nano-catalysis, electrolysis, flocculation and air-floatation device | |
CN101113031A (en) | Method for treating oil field wastewater by electro-float process | |
CN209759191U (en) | Device for treating livestock and poultry wastewater by virtue of electric flocculation and ozone nano-bubble air flotation | |
CN103601337A (en) | Device for removing washing agent from restaurant wastewater | |
CN103723867B (en) | A kind of economic benefits and social benefits air bearing algae blooms water processing equipment and its treatment process | |
CN105347582B (en) | A kind of device and method of iron-carbon micro-electrolysis degrading alkaline organic wastewater | |
CN105923911A (en) | Refuse leachate pretreatment method | |
CN206538318U (en) | A kind of device for handling the high organic wastewater of industrial high salt | |
CN202898140U (en) | System for recycling oil-containing washing waste water | |
CN1216813C (en) | Method and equipment for oil field waste water treatment | |
CN105621761B (en) | A kind of oilfield produced water processing method, processing unit | |
CN2579880Y (en) | Oil field waste water treating device | |
CN208814844U (en) | Oil-containing sewage treatment system | |
CN209397010U (en) | The anti-disturbance three-level settling tank of electroplating sewerage | |
CN203878006U (en) | Electroprocessing sewage purifying and recycling system | |
CN208218448U (en) | A kind of spraying waste water air-floating processing apparatus | |
CN206590935U (en) | Multi-functional electroxidation water purifier | |
CN105776684A (en) | Urban sewage treatment and resource recycling method | |
CN208857094U (en) | Chemical industry washing procedure wastewater treatment equipment | |
CN110902875A (en) | Oil-gas field produced water treatment system and method based on ozone air floatation device | |
CN104230055A (en) | Refinery wastewater treatment method | |
CN205328819U (en) | Low energy consumption MBR integration sewage treatment device | |
CN205347123U (en) | Traditional chinese medicine effluent disposal system | |
CN105645690B (en) | The processing system of detergent in a kind of removal sanitary wastewater | |
CN105540952B (en) | Murexide waste water treatment process |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C02 | Deemed withdrawal of patent application after publication (patent law 2001) | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20080130 |