CN108975629A - A kind of sewage treatment process of high oil mass - Google Patents
A kind of sewage treatment process of high oil mass Download PDFInfo
- Publication number
- CN108975629A CN108975629A CN201810950771.5A CN201810950771A CN108975629A CN 108975629 A CN108975629 A CN 108975629A CN 201810950771 A CN201810950771 A CN 201810950771A CN 108975629 A CN108975629 A CN 108975629A
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- sewage
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Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/38—Treatment of water, waste water, or sewage by centrifugal separation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5263—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using natural chemical compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular compounds
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/08—Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
Abstract
The invention discloses a kind of sewage treatment process of high oil mass, bio-aeration by carrying out gradation in batches to the high trade effluent of oil content is handled, by precipitating pretreatment, anaerobism, flocculation treatment and etc. combine, simple process, effect is good, percent of decolourization, oily waste degradation rate is high, COD, BOD removal rate, tp removal rate is high, solid residues amount is small, and low in cost, is suitble to promote.
Description
Technical field
The present invention relates to a sewage water treatment method, in particular to a kind of sewage treatment process of high oil mass.
Background technique
With China's industrial development, a large amount of trade effluents and sanitary sewage are produced, pollution on the environment influence is got over
Come more next obvious.The highly difficult sewage wherein discharged, such as chemical engineering sewage, petrifaction sewage, coked waste water, landfill leachate, pharmacy
Sewage, plating cyanogens-containing sewage water, grinding sewage etc., contain many refractory organics and bio-toxicity object in these sewage
Matter, organic components are complicated, and COD COD concentration is high, and such sewage is very difficult.In recent years, China is highly difficult
Field of sewage treatment has many researchs and technological development, but corresponding environmentally friendly task is still very arduous.
Particularly with the sewage that petrochemical industry processing generates, in such sewage in not only oil slick, oil emulsion and dissolved oil content
Height, but also a large amount of suspended organic matter can be contaminated with, and in above-mentioned suspended organic matter ingredient usually can containing phenol, aldehyde,
The substance of the degradabilities such as alcohol, alkane, halogenated hydrocarbons difference, therefore substantially increase the processing difficulty of the high sewage of oil content.
Summary of the invention
The invention aims to solve the above problems, a kind of sewage treatment process of high oil mass is provided.
In order to achieve the above objectives, the method that the present invention uses is: a kind of sewage treatment process of high oil mass, including following
Step:
(1) using sewage pump by sewage through the coarse solid sundries in grid decontamination water, then by sewage be sent into setting pot in into
Row precipitation process;
(2) sewage in sedimentation basin is sent into aeration and biological pond and is handled;
(3) it will handle by treated in aeration and biological pond sewage being sent into anaerobic pond;
(4) sewage crossed through Anaerobic Treatment is sent into anoxic zone and carries out anoxic treatment;
(5) sewage is sent into flocculation tank and is handled, add flocculant, flocculant usage is sewage 200- per ton
280g makes to handle a large amount of colloidal solids in water and completes flocculation;
(6) after the sewage in step (5) after flocculating being carried out secondary precipitation, and sediment is separated by cyclone separator;
(7) sewage of step (6) separation is being passed through into adsorption treatment, activated coke, and filling in blender is added in adsorption tank
Divide under stirring and comes into full contact with the water outlet after the activated coke and biochemical treatment of powder shape;
(8) passing through step (7), treated by the filtering of filler filter layer.
As an improvement of the present invention, the ingredient of the flocculant are as follows: the ferric sulfate of 5-12 parts by weight, 10-15 weight
Measure the ferric trichloride of part, the ferrate of 5-10 parts by weight;Polyacrylamide, gelatin, the soluble cellulose of 8-15 parts by weight
Mixture.
The utility model has the advantages that
The present invention is handled by the bio-aeration for carrying out gradation in batches to the high trade effluent of oil content, pre-processed by precipitating,
Anaerobism coupling technique and flocculation treatment and etc. combine, simple process, effect is good, percent of decolourization, oily waste degradation rate
Height, COD, BOD removal rate, tp removal rate is high, and solid residues amount is small, and low in cost, is suitble to promote.
Specific embodiment:
Below with reference to specific embodiment, the present invention is further described;
Embodiment 1:
A kind of sewage treatment process of high oil mass, comprises the following steps that
(1) using sewage pump by sewage through the coarse solid sundries in grid decontamination water, then by sewage be sent into setting pot in into
Row precipitation process;
(2) sewage in sedimentation basin is sent into aeration and biological pond and is handled;
(3) it will handle by treated in aeration and biological pond sewage being sent into anaerobic pond;
(4) sewage crossed through Anaerobic Treatment is sent into anoxic zone and carries out anoxic treatment;
(5) sewage to be sent into flocculation tank and is handled, add flocculant, flocculant usage is dirt 200-280g per ton,
Make to handle a large amount of colloidal solids in water and completes flocculation;
(6) after the sewage in step (5) after flocculating being carried out secondary precipitation, and sediment is separated by cyclone separator;
(7) sewage of step (6) separation is being passed through into adsorption treatment, activated coke, and filling in blender is added in adsorption tank
Divide under stirring and comes into full contact with the water outlet after the activated coke and biochemical treatment of powder shape;
(8) passing through step (7), treated by the filtering of filler filter layer.
The ingredient of above-mentioned flocculant are as follows: the ferric sulfate of 5-12 parts by weight, the ferric trichloride of 10-15 parts by weight, 5-10 weight
Measure the ferrate of part;The polyacrylamides of 8-15 parts by weight, gelatin, soluble cellulose mixture.
Claims (2)
1. a kind of sewage treatment process of high oil mass, it is characterised in that: comprise the following steps that
(1) using sewage pump by sewage through the coarse solid sundries in grid decontamination water, then by sewage be sent into setting pot in into
Row precipitation process;
(2) sewage in sedimentation basin is sent into aeration and biological pond and is handled;
(3) it will handle by treated in aeration and biological pond sewage being sent into anaerobic pond;
(4) sewage crossed through Anaerobic Treatment is sent into anoxic zone and carries out anoxic treatment;
(5) sewage is sent into flocculation tank and is handled, add flocculant, flocculant usage is sewage 200- per ton
280g makes to handle a large amount of colloidal solids in water and completes flocculation;
(6) after the sewage in step (5) after flocculating being carried out secondary precipitation, and sediment is separated by cyclone separator;
(7) sewage of step (6) separation is being passed through into adsorption treatment, activated coke, and filling in blender is added in adsorption tank
Divide under stirring and comes into full contact with the water outlet after the activated coke and biochemical treatment of powder shape;
(8) passing through step (7), treated by the filtering of filler filter layer.
2. a kind of sewage treatment process of high oil mass according to claim 1, it is characterised in that: the flocculant at
It is divided into: the ferric sulfate of 5-12 parts by weight, the ferric trichloride of 10-15 parts by weight, the ferrate of 5-10 parts by weight;8-15 parts by weight
Polyacrylamide, gelatin, soluble cellulose mixture.
Priority Applications (1)
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CN201810950771.5A CN108975629A (en) | 2018-08-20 | 2018-08-20 | A kind of sewage treatment process of high oil mass |
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CN201810950771.5A CN108975629A (en) | 2018-08-20 | 2018-08-20 | A kind of sewage treatment process of high oil mass |
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CN108975629A true CN108975629A (en) | 2018-12-11 |
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CN201810950771.5A Pending CN108975629A (en) | 2018-08-20 | 2018-08-20 | A kind of sewage treatment process of high oil mass |
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN114262120A (en) * | 2021-12-20 | 2022-04-01 | 山东恒鑫生物科技有限公司 | Gelatin wastewater treatment process beneficial to environmental protection |
Citations (9)
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US4354941A (en) * | 1980-03-10 | 1982-10-19 | Georg Ronge | Process for continuous separation of polluting matter from a carrier fluid |
CN1669956A (en) * | 2004-03-18 | 2005-09-21 | 昆明柯利欣环保科技有限公司 | High efficiency sewage treatment method |
CN101264999A (en) * | 2008-04-23 | 2008-09-17 | 山东大学 | Process and apparatus for treating sewage |
CN101428945A (en) * | 2008-12-15 | 2009-05-13 | 上海埃梯梯恒通先进水处理有限公司 | Method and apparatus for treating and recycling carbonized wastewater |
CN101525576A (en) * | 2009-04-14 | 2009-09-09 | 中华绿油有限公司 | Method for producing microalgae with domestic sewage and industrial sewage |
CN101781067A (en) * | 2010-03-23 | 2010-07-21 | 哈尔滨工业大学 | Method for treating coking wastewater |
CN101781066A (en) * | 2010-03-23 | 2010-07-21 | 哈尔滨工业大学 | Caffeine production wastewater treatment method |
CN102531283A (en) * | 2011-12-30 | 2012-07-04 | 南昌大学 | Method for treating food processing organic wastewater containing high-concentration fat and suspended matter |
CN104276729A (en) * | 2014-10-16 | 2015-01-14 | 滁州友林科技发展有限公司 | High-oil-content sewage treatment technique |
-
2018
- 2018-08-20 CN CN201810950771.5A patent/CN108975629A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4354941A (en) * | 1980-03-10 | 1982-10-19 | Georg Ronge | Process for continuous separation of polluting matter from a carrier fluid |
CN1669956A (en) * | 2004-03-18 | 2005-09-21 | 昆明柯利欣环保科技有限公司 | High efficiency sewage treatment method |
CN101264999A (en) * | 2008-04-23 | 2008-09-17 | 山东大学 | Process and apparatus for treating sewage |
CN101428945A (en) * | 2008-12-15 | 2009-05-13 | 上海埃梯梯恒通先进水处理有限公司 | Method and apparatus for treating and recycling carbonized wastewater |
CN101525576A (en) * | 2009-04-14 | 2009-09-09 | 中华绿油有限公司 | Method for producing microalgae with domestic sewage and industrial sewage |
CN101781067A (en) * | 2010-03-23 | 2010-07-21 | 哈尔滨工业大学 | Method for treating coking wastewater |
CN101781066A (en) * | 2010-03-23 | 2010-07-21 | 哈尔滨工业大学 | Caffeine production wastewater treatment method |
CN102531283A (en) * | 2011-12-30 | 2012-07-04 | 南昌大学 | Method for treating food processing organic wastewater containing high-concentration fat and suspended matter |
CN104276729A (en) * | 2014-10-16 | 2015-01-14 | 滁州友林科技发展有限公司 | High-oil-content sewage treatment technique |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN114262120A (en) * | 2021-12-20 | 2022-04-01 | 山东恒鑫生物科技有限公司 | Gelatin wastewater treatment process beneficial to environmental protection |
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Application publication date: 20181211 |