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CN102964027B - Culture wastewater treatment method - Google Patents

Culture wastewater treatment method
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Publication number
CN102964027B
CN102964027BCN201210454362.9ACN201210454362ACN102964027BCN 102964027 BCN102964027 BCN 102964027BCN 201210454362 ACN201210454362 ACN 201210454362ACN 102964027 BCN102964027 BCN 102964027B
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China
Prior art keywords
wash
down water
water
waste liquor
rinsing water
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Expired - Fee Related
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CN201210454362.9A
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Chinese (zh)
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CN102964027A (en
Inventor
董部根
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GUANGZHOU BACON YU AGRICULTURAL BIOTECHNOLOGY Ltd Co
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GUANGZHOU BACON YU AGRICULTURAL BIOTECHNOLOGY Ltd Co
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Priority to CN201210454362.9ApriorityCriticalpatent/CN102964027B/en
Publication of CN102964027ApublicationCriticalpatent/CN102964027A/en
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Abstract

The invention discloses a culture wastewater treatment method which comprises the following steps: A. separating wastewater into rinsing water and waste liquor, and respectively collecting the rinsing water and waste liquor; B. treating the collected rinsing water to achieve the culture wastewater discharge standard; C. concentrating the separated waste liquor in the step A to obtain a concentrated solution and a clear solution; D. recycling the concentrated clear solution, and fermenting the concentrated solution; and E. using the fermented concentrated solution as a liquid fertilizer. The culture wastewater is classified to separate the waste liquor containing high-concentration NH3-N and the high-COD (chemical oxygen demand) rinsing water. After the separation, the high-NH3-N waste liquor and the high-COD rinsing water are respectively treated, thereby avoiding the mutual influence between the NH3-N and COD. The treated waste liquor is used as the liquid fertilizer, thereby providing high-quality fertilizer resources for agriculture. The treated rinsing water is superior to the culture wastewater discharge standard, thereby implementing discharge of culture wastewater after reaching the standard or recycling of reclaimed water, and being energy-saving and environment-friendly. The invention is used in the field of wastewater treatment.

Description

A kind of breeding wastewater treatment process
Technical field
The present invention relates to a kind for the treatment of process of waste water, particularly relate to a kind for the treatment of process of breeding wastewater.
Background technology
Effective improvement of Stock raising waste, has become one of Three Difficult Issues of puzzlement world environments worker.With regard to its quantity discharged, it is industry and urban life waste discharge amount 2 times that its organism be take quantity discharged that COD is equivalent.More bad, industry and urban life waste effectively administered, and the improvement of China's breeding waste also rest on do not process or simply dealt situation under.
Why aquaculture sewage is difficult to process, and its major cause is in sewage, mainly to contain ight soil urine, wherein organism (COD), ammonia nitrogen (NH3-N) and the concentration of total phosphorus (TP) high, be tens of even hundreds of times of most of industrial sewage and sanitary sewage, its intractability and processing cost are well imagined.
The conventional treatment process of breeding wastewater is anaerobism (biogas) technique+anoxic+aerobic+chemical dephosphorization+oxidation pond at present.Common process, for the COD that effectively degrades, uses the organic carbon in sewage, has strengthened anaerobic treatment, because anaerobic technique is hydrolysis, acidifying, methanogenic process at leading portion.Enough when the anaerobic technique residence time, design is enough reasonable, and a large amount of organic carbons can constantly resolve into CH4, C2h6deng air release out, the range of decrease of COD is greatly improved.Make so a large amount of organic carbons can absorb as biogas energy, the difficulty of the COD of subsequent technique degraded simultaneously significantly reduces.
But the simultaneous aminating reaction of anaerobic process, makes the NH in sewage3-N has increased 20-30%, NH when entering subsequent handling3the treating processes of-N is completed by ammonification (anaerobism) → nitrated (aerobic) → denitrification (anoxic).By this three-step reaction, it is fully decomposed, simultaneously NH3the removal of-N, must have corresponding carbon source as the prerequisite of anti-nitration reaction.Generally C:N is than could effectively carry out denitrification more than 4:1.By the technological design of current breeding wastewater main flow, the water outlet C:N ratio of sewage after anaerobic and aerobic are processed is almost 1:1, realize C:N ratio more than 4:1, needs 400% quantity of reflux.Reflux ratio rises greatly, although to NH3the treatment effect of-N has ensured, but the biochemical section of system is subject to the impact of 4 times of above impact loads, and the effect of each technique unit just cannot effectively be controlled, and thus, the design of technological process processing parameter is controlled difficulty and greatly strengthened.
Summary of the invention
For addressing the above problem, the invention provides a kind of effective solution and remove COD and NH in waste water3the breeding wastewater treatment process of-N contradiction.
The technical solution adopted for the present invention to solve the technical problems is:
A breeding wastewater treatment process, comprises the following steps:
A. by effluent segregation, be wash-down water and waste liquid, and collect respectively;
B. the wash-down water of collecting is processed, made it to reach breeding wastewater emission standard;
C. the waste liquid distributing in steps A is carried out to concentration, and obtain dope and clear liquid;
D. by the concentrated clear liquid recycling obtaining, the concentrated dope obtaining is carried out to fermentative processing;
E. the dope after fermentative processing is made to liquid biological organic fertilizer.
Be further used as the improvement of technical solution of the present invention, adopt 3-way valve to control the shunting of waste water in steps A, while not rinsing cultivation place, 3-way valve is not controlled and is collected waste liquid, and when water rinses, 3-way valve is controlled and collected wash-down water.
Be further used as the improvement of technical solution of the present invention, in step B, wash-down water passes through the processing of baffling type anaerobic reactor and BAF successively, removes the pollutent in wash-down water, completes the carbon elimination of wash-down water, nitrated, denitrogenation, dephosphorization and processes.
Be further used as the improvement of technical solution of the present invention, during fermentative processing in step D, in dope, add organic high phosphorus, high potassium material, middle trace element and microbial preparation.
Beneficial effect of the present invention: first this breeding wastewater treatment process classifies to breeding wastewater, will be containing high density NH3the waste liquid of-N and the shunting of the wash-down water of high COD.After shunting, then process respectively high NH3the waste liquid of-N and the wash-down water of high COD, avoided combination treatment NH3the interactional contradiction of-N and COD, the waste liquid after simultaneously processing is made liquid fertilizer, and for agricultural provides the manure resources of high-quality, wash-down water after treatment, is better than breeding wastewater emission standard, realizes qualified discharge or the middle water reuse of breeding wastewater, not only energy-conservation but also environmental protection.
Accompanying drawing explanation
Below in conjunction with accompanying drawing, the invention will be further described:
Fig. 1 is embodiment of the present invention schematic flow sheet.
Embodiment
With reference to Fig. 1, of the present invention a kind of breeding wastewater treatment process disclosed, comprise the following steps:
A. by effluent segregation, be wash-down water and waste liquid, and collect respectively;
B. the wash-down water of collecting is processed, made it to reach breeding wastewater emission standard;
C. the waste liquid distributing in steps A is carried out to concentration, and obtain dope and clear liquid;
D. by the concentrated clear liquid recycling obtaining, the concentrated dope obtaining is carried out to fermentative processing;
E. the dope after fermentative processing is made to liquid biological organic fertilizer.
Breeding wastewater main component is animal excrements and feed, and first this breeding wastewater treatment process classifies to breeding wastewater, will be containing high density NH3the waste liquid of-N and the shunting of the wash-down water of high COD.After shunting, then process respectively high NH3the waste liquid of-N and the wash-down water of high COD, avoided combination treatment NH3the interactional contradiction of-N and COD, the waste liquid after simultaneously processing is made liquid fertilizer, and for agricultural provides the manure resources of high-quality, wash-down water after treatment, is better than breeding wastewater emission standard, realizes qualified discharge or the middle water reuse of breeding wastewater, not only energy-conservation but also environmental protection.
As the preferred embodiment of the present invention, in steps A, adopt 3-way valve to control the shunting of waste water, while not rinsing cultivation place, 3-way valve is not controlled and is collected waste liquid, and when water rinses, 3-way valve is controlled and is collected wash-down water.
For the cleaning of cultivation waste liquid, while not rinsing cultivation place, 3-way valve is not controlled waste liquid and is imported waste collection pond, and while rinsing cleaning, 3-way valve is controlled wash-down water and imported wash-down water collecting tank, completes high NH3the shunting of the waste liquid of-N and the wash-down water of high COD.
As the preferred embodiment of the present invention, in step B, wash-down water passes through the processing of baffling type anaerobic reactor and BAF successively, removes the pollutent in wash-down water, completes the carbon elimination of wash-down water, nitrated, denitrogenation, dephosphorization and processes.
In baffling type anaerobic reactor, realize hydrolysis, acidifying, the methanogenic process of wash-down water.Enough when the anaerobic technique residence time, a large amount of organic carbons can constantly resolve into CH4, C2h6deng air release out, the range of decrease of COD is greatly improved, a large amount of organic carbons can be absorbed as biogas energy, the difficulty of the COD of subsequent technique degraded simultaneously significantly reduces, anaerobic reactor is in the methanogenic process of acidication, for the aminating reaction of while output provides nitrification and denitrification condition, make NH in reactor water outlet3-N obviously declines, and by BAF, is further removed and comprises SS, COD, BOD, NH3-N, TP, complete the carbon elimination of wash-down water, nitrated, denitrogenation, dephosphorization and process.
As the preferred embodiment of the present invention, during fermentative processing in step D, in dope, add organic high phosphorus, high potassium material, middle trace element and microbial preparation.
Fermentative processing is mainly for NH in dope3the processing of-N, NH3the treating processes of-N is completed by ammonification (anaerobism) → nitrated (aerobic) → denitrification (anoxic), during processing, in dope, add organic high phosphorus, high potassium material, middle trace element and microbial preparation, guarantee that fermentation carries out smoothly, and obtain the liquid biological fertilizer of high-quality, high quality, the biological insect protected of tool, diseases prevention.
Certainly, the invention is not limited to above-mentioned embodiment, those of ordinary skill in the art also can make equivalent variations or replacement under the prerequisite without prejudice to spirit of the present invention, and the modification that these are equal to or replacement are all included in the application's claim limited range.

Claims (1)

CN201210454362.9A2012-11-132012-11-13Culture wastewater treatment methodExpired - Fee RelatedCN102964027B (en)

Priority Applications (1)

Application NumberPriority DateFiling DateTitle
CN201210454362.9ACN102964027B (en)2012-11-132012-11-13Culture wastewater treatment method

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Application NumberPriority DateFiling DateTitle
CN201210454362.9ACN102964027B (en)2012-11-132012-11-13Culture wastewater treatment method

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CN102964027Btrue CN102964027B (en)2014-10-29

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Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication numberPriority datePublication dateAssigneeTitle
CN103172244B (en)*2013-03-262014-12-31广州培根裕农生物科技有限公司Recycling treatment method of water-submerged manure in breeding industry
CN103601346A (en)*2013-12-042014-02-26苏理黔Method for producing liquid active ecological organic raw material by adopting breeding wastewater
CN109133516A (en)*2018-09-182019-01-04广西大学A kind of breeding wastewater resource utilization utilizes method
CN108976060A (en)*2018-10-102018-12-11徽县绿源科技开发有限责任公司A kind of water soluble fertilizer processed using Wastewater from Pig Farm
CN109619017A (en)*2018-12-292019-04-16广州创领水产科技有限公司A kind of environment-friendly type industrial circulating water cultivating technology and system
CN109455888A (en)*2019-01-022019-03-12云南正辰环境科技有限公司A kind of processing method of livestock breeding wastewater
CN112897707B (en)*2021-01-152023-03-28四川渔光物联技术有限公司Tail water treatment device

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JP2006348191A (en)*2005-06-162006-12-28Chugoku Electric Power Co Inc:TheSystem for circulating biomass
CN101020593A (en)*2006-04-062007-08-22上海百峰环保工程有限公司Process of treating sewage with animal's excrement
CN201777956U (en)*2010-04-142011-03-30南昌大学Sequencing batch biofilm reactor processing system for piggery wastewater
CN102642985A (en)*2012-04-232012-08-22南京师范大学Method and system for treatment and recycling of feces and waste from livestock and poultry culture
CN102718355A (en)*2012-05-212012-10-10杨欣Breeding pollution discharge treatment system and treatment method thereof

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication numberPriority datePublication dateAssigneeTitle
JP2006348191A (en)*2005-06-162006-12-28Chugoku Electric Power Co Inc:TheSystem for circulating biomass
CN101020593A (en)*2006-04-062007-08-22上海百峰环保工程有限公司Process of treating sewage with animal's excrement
CN201777956U (en)*2010-04-142011-03-30南昌大学Sequencing batch biofilm reactor processing system for piggery wastewater
CN102642985A (en)*2012-04-232012-08-22南京师范大学Method and system for treatment and recycling of feces and waste from livestock and poultry culture
CN102718355A (en)*2012-05-212012-10-10杨欣Breeding pollution discharge treatment system and treatment method thereof

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