CN101792340B - Pig manure centralized treatment and resource utilization method - Google Patents
Pig manure centralized treatment and resource utilization method Download PDFInfo
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- CN101792340B CN101792340B CN2010101355385A CN201010135538A CN101792340B CN 101792340 B CN101792340 B CN 101792340B CN 2010101355385 A CN2010101355385 A CN 2010101355385A CN 201010135538 A CN201010135538 A CN 201010135538A CN 101792340 B CN101792340 B CN 101792340B
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/20—Sludge processing
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
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Abstract
The invention discloses a pig manure centralized treatment and resource utilization method, which comprises processes of pretreatment, squeezing treatment, biogas production, biogas purification, biogas power generation, biogas slurry separation, guanite crystallization, residual liquid treatment and composting treatment, wherein a biological treatment process is set to be combined with a series of resource recovery strategies so as to realize the zero-emission treatment of the pig manure, and thereby the working environment and the peripheral environment of a hoggery are greatly improved, and the environmental protection and the comprehensive treatment of the hoggery are benefited; the whole process is better integrated, can be combined into an integral device, also can be modularly divided into a functional module of a biogas production generating system, a water purification functional module in high-concentration hoggery sewage and a special-effect organic fertilizer production functional module, and the whole facility occupies small area, has lower investment and operational cost, and is easy to realize equipping; and the invention organically combines the production of biogas, electricity generation, organic fertilizer and guanite, and has good social and economic benefits.
Description
Technical field
The present invention relates to pig manure Treatment Technology field, pig farm, particularly a kind of pig manure material focuses on and utilization of resources method.
Background technology
At present general large-scale pig farm all can produce the pig manure about 10 tons every day; Adopt the nature pattern of banking up on the most pig farm of China; Muck directly mixed with dry-matteies such as stalk, sawdusts carry out long-time compost after stirring, the composting time is needs 6 months often, or could accomplish for more time.In the prior art, put down in writing for the following document of mainly containing of pig manure:
1, be that document " with the method for preparing highly efficient organic fertilizer from dungs and droppings " (notification number is CN1962559A) is applied for a patent in the China invention of ZL200610070510.1 like the patent No.; May further comprise the steps: mix and stir: feces of livestock and poultry, stopping composition and microbial starter culture thorough mixing are stirred; Pack, sign indicating number heap, fermentation dried: regular stacking earlier, pile through a sign indicating number heap-turning-sign indicating number then, get work in-process; Granulation; Pack, sign indicating number heap, fermentation dried; Pack; Wherein feces of livestock and poultry is pig manure, cow dung, chicken manure, duck excrement, and stopping composition is offal and rice bran, and microbial starter culture is the EM biological bacteria preparation.The method that the document provided; Just carried out simple processing to feces of livestock and poultry, though shortened the Production Time of fertilizer in time, lower to the comprehensive utilization ratio of feces of livestock and poultry; Used electric weight etc. all need the outside to provide, and the overall energy consumption that produces is higher.
2, be that document " processing of pig manure and utilize method " (notification number is CN101429057A) is applied for a patent in the China invention of ZL200810045547.8 like the patent No.; Comprise: 1. regulate moisture: fresh pig dung stirs, mixes with dried pig manure process, and water ratio drops to 55～60%.2. breeding earthworm: pig manure is deposited on the earthworm bed, drops into earthworm kind breeding earthworm.3. feed: the oven dry earthworm joins in the feed base-material and fits in high protein feed.4. fermentation: in the fermentation booth, pig manure carries out continuous aerobic fermentation to be handled, 5～7 days cycles, turned over throwing once in per 2 hours, and inject fresh air simultaneously, water ratio drops to 40～45%.5. dry: pig manure carries out drying treatment in pneumatic drier, water ratio drops to below 14%.6. deodorizing is handled: tail gas carries out deodorizing through wet dust collector to be handled.7. edible mushrooms base-material: pig manure is added in the fillers such as straw joint, wheat straw joint, process the base-material of culturing edible fungus.This method has been introduced the way of breeding earthworm, but whole making place is bigger, and human cost increases; And need be by a large amount of external electric energy in drying process, whole work efficiency is lower.
3, be that document " a kind of pig manure is produced the method for biological organic fertilizer " (notification number is CN101565331A) is applied for a patent in the China invention of ZL200810149876.7 like the patent No.; Moisture about 65% fresh pig dung and suitable proportion saw is unmixed; Make its carbon: nitrogen is than between 16-25; Stir with geotrichum sp or bacstearothermophilus fermenting agent then and carry out compost fermentation, turning is regularly treated that temperature of charge is reduced to dry after the envrionment temperature or air-dry; Pulverize, be the refined biometric fertilizer.Its nutrient content reaches 7%, and organic content reaches more than 50%.This method has adopted produces fertilizer with pig manure and the low dry-matter method of mixing of water ratio, and fails a large amount of nitrogen, the phosphoric that contain in the pig manure are extracted recovery; And the composting process cycle is long, and whole efficient is lower.
4, be that document " a kind of treatment process of zero pollution of waste of pig farm " (notification number is CN101531441A) is applied for a patent in the China invention of ZL200910043126.6 like the patent No.; Processing such as stable, pulverizing by fermentation,, screening; The refined organic fertilizer of the market competitiveness is conveniently used, had to output; It comprises with domestic animal pig urine collecting import methane-generating pit, anaerobically fermenting, inflow fermentation vat, with straw powder with its absorption, the pig manure that changes acidulated pool acidifying and pig manure collecting tank over to stir, nurse one's health, adjustment, one time fermentation, Secondary Fermentation, stable, pulverize, sieve, fines is processed into refined organic fertilizer; Coarse fodder returns to fermentation vat and mixes with natural pond liquid absorption reprocessing fines, output refined organic fertilizer with straw powder; Sow cub's in the field placenta, dead without reason domestic animal pig corpse were put into the burning of biogas incinerator the same day, and flue gas gets into the ventilation storehouse, bottom of stablizing the storehouse, after fertilizer filters, discharges, and residue is sent in the fermentation tower, becomes refined organic fertilizer through processing output.Adopted the dry-matter method of mixing that water ratio such as pig manure and stalk is low to produce fertilizer; And fail a large amount of nitrogen, the phosphoric that contain in the pig manure are extracted recovery; And the composting process steps is loaded down with trivial details, and the production cycle is long, and is lower to the comprehensive utilization ratio of swine excrement.
Summary of the invention
Technical problem to be solved by this invention is the present situation to prior art, provide that a kind of technical process is reasonable, comprehensive utilization ratio is high, realize the pig manure zero release, whole facility floor space is little and the fertilizer composting fast the pig manure material focus on and utilization of resources method.
The present invention solves the problems of the technologies described above the technical scheme that is adopted: a kind of pig manure material focuses on and utilization of resources method, includes pre-treatment step: the pig manure material is poured in the manure lagoon, and carry out the preliminary adjusting of water ratio; Also include following steps:
The squeezing treatment step: the pig manure material in the manure lagoon is delivered in the press apparatus through lift pump, transport pipe, and the pig manure material is handled through squeezing, liquid excrement slurry;
Biogas produces step: the liquid excrement slurry after squeezing is handled gets into the excrement slurry and produces natural pond equipment, produces the production that natural pond equipment is realized biogas by the excrement slurry;
The marsh gas purifying step: excrement slurry produce that natural pond equipment produced biogas get in the marsh gas purifying equipment through pneumatic tube, and the biogas of input is carried out purifying treatment;
The marsh gas power generation step: the biogas after the purifying treatment inputs in the biogas generator after the gas-holder regulating, and biogas generator is launched and generated electricity;
Natural pond liquid separating step: the excrement slurry produces and is left that natural pond liquid thing is arranged after natural pond equipment produces the natural pond, and this natural pond liquid thing inputs to solid-liquid separating equipment, and isolates the excrement slag of solid attitude and the pending liquid of liquid state; The excrement slag of solid attitude is directly fallen in the high temperature aerobic composting facility;
Struvite crystallisation step: in the isolating pending liquid input struvite crystalline element of solid-liquid separating equipment institute, add magnesia mixture, extract and obtain the struvite crystallization; And pending liquid also produces after the struvite crystallization has residual liquid, and nitrogen element and phosphoric in this residual liquid are extracted;
The residual solution treatment step: remaining residual liquid is sprayed in the high temperature aerobic composting facility through shower in the struvite crystalline element; After the residual liquid reuse, still have remainder water liquid, it gets in the unit for treating water, carries out processing up to standard;
The compost treatment step: the bottom of high temperature aerobic composting facility is a fermentation bed, and the excrement slag of output all is piled up on this fermentation bed in the solid-liquid separating equipment, and controls the aerobic fermentation of excrement slag by fermentation bed; The high temperature aerobic composting facility also disposes temperature control system and gas blower, and the real time temperature of temperature control system monitor fermentation bed, and the water spray of shower and the air quantity of gas blower are carried out feedback control.
The measure of taking also comprises:
In the above-mentioned squeezing treatment step, the pig manure material reaches 45% to 70% through its water ratio of liquid excrement slurry that squeezing is processed into.
In the above-mentioned squeezing treatment step, press apparatus also can be isolated the excrement slag in treating processes, and this excrement slag is directly fallen in the high temperature aerobic composting facility.
In the above-mentioned marsh gas power generation step, the generating of biogas generator institute is connected with lift pump, solid-liquid separating equipment, temperature control system, gas blower, promptly forms the EPS of internal system.
In the above-mentioned residual solution treatment step, remaining residual liquid also can return back in the manure lagoon through return line in the struvite crystalline element.
Compared with prior art, pre-treatment step, squeezing treatment step, biogas generation step, marsh gas purifying step, marsh gas power generation step, natural pond liquid separating step, struvite crystallisation step, residual solution treatment step and compost treatment step have been the present invention includes; The invention has the advantages that: biological treatment process is set and a series of resource recovery measure is harmonious, realizes the zero discharge treatment of pig manure, improved the Working environment and the surrounding enviroment on pig farm greatly, be beneficial to the environment protection and the comprehensive regulation of place; Whole flow process has good integration; Can be combined to integral device; Also but modularization is divided into water purifying function module and special efficacy organic fertilizer production functional module in product natural pond power generation system functional module, the high density pig farm sewage; Whole facility floor space is little, and investment and running cost are lower, are easy to the equipmentization that realizes; The production of biogas, generating, fertilizer and struvite is organically combined, have good social benefit and economic benefit.
Description of drawings
Fig. 1 is a treatment process principle schematic of the present invention.
Embodiment
Embodiment describes in further detail the present invention below in conjunction with accompanying drawing.
As shown in Figure 1, the embodiment of the invention, its structure be by manure lagoon 1, lift pump 2, transport pipe 3; Press apparatus 4, the excrement slurry produces natural pond equipment 5, pneumatic tube 6, marsh gas purifying equipment 7 is through gas-holder 8; Biogas generator 9, solid-liquid separating equipment 10, struvite crystalline element 11, unit for treating water 12, high temperature aerobic composting facility 13; Shower 14, return line 15, temperature control system 16, gas blower 17 constitutes.
A kind of pig manure material focuses on and utilization of resources method, includes pre-treatment step: the pig manure material is poured in the manure lagoon 1, and carry out the preliminary adjusting of water ratio; Also include following steps:
The squeezing treatment step: the pig manure material in the manure lagoon 1 is delivered in the press apparatus 4 through lift pump 2, transport pipe 3, and the pig manure material is handled through squeezing, liquid excrement slurry;
Biogas produces step: the liquid excrement slurry after squeezing is handled gets into the excrement slurry and produces natural pond equipment 5, produces the production that natural pond equipment 5 is realized biogas by the excrement slurry;
The marsh gas purifying step: excrement slurry produce that natural pond equipment 5 produced biogas get in the marsh gas purifying equipment 7 through pneumatic tube 6, and the biogas of input is carried out purifying treatment;
The marsh gas power generation step: the biogas after the purifying treatment inputs in the biogas generator 9 after gas-holder 8 regulating, and biogas generator 9 is launched and generated electricity;
Natural pond liquid separating step: the excrement slurry is left that natural pond liquid thing is arranged after producing equipment 5 product natural ponds, natural pond, and this natural pond liquid thing inputs to solid-liquid separating equipment 10, and isolates the excrement slag of solid attitude and the pending liquid of liquid state; The excrement slag of solid attitude is directly fallen in high temperature aerobic composting facility 13;
Struvite crystallisation step: in 10 isolating pending liquid input struvite crystalline elements 11 of solid-liquid separating equipment, add magnesia mixture, extract and obtain the struvite crystallization; And pending liquid also produces after the struvite crystallization has residual liquid, and the COD value of residual liquid has been reduced to lower level, and nitrogen element and phosphoric in this residual liquid are extracted;
The residual solution treatment step: remaining residual liquid is sprayed in the high temperature aerobic composting facility 13 through shower 14 in the struvite crystalline element 11; After the residual liquid reuse, still have remainder water liquid, it gets in the unit for treating water 12, carries out processing up to standard;
The compost treatment step: the bottom of high temperature aerobic composting facility 13 is a fermentation bed, and the excrement slag of output all is piled up on this fermentation bed in the solid-liquid separating equipment 10, and controls the aerobic fermentation of excrement slag by fermentation bed; High temperature aerobic composting facility 13 also disposes temperature control system 16 and gas blower 17, and the real time temperature of temperature control system 16 monitor fermentation beds, and the water spray of shower 14 and the air quantity of gas blower 17 are carried out feedback control.
In the squeezing treatment step, the pig manure material reaches 45% to 70% through its water ratio of liquid excrement slurry that squeezing is processed into.In the squeezing treatment step, press apparatus 4 also can be isolated the excrement slag in treating processes, and this excrement slag is directly fallen in high temperature aerobic composting facility 13.In the marsh gas power generation step, 9 generatings of biogas generator are connected with lift pump 2, solid-liquid separating equipment 10, temperature control system 16, gas blower 17, promptly form the EPS of internal system.In the residual solution treatment step, remaining residual solution also can return back in the manure lagoon 1 through return line 15 in the struvite crystalline element 11.
Adopt and produce water purifying function module and special efficacy organic fertilizer production functional module three big unit combination treatment thinkings in natural pond electricity generate function module, the high density pig farm sewage; Water purifying function module in the sewage of high density pig farm: adopt zeyssatite microcarrier reinforced jet aeration process, residual complicated organism to strengthen contact degradation technique, the efficient clarification technique three big technology that suspend; Finally carry out processing up to standard; Adopt integrated-type treatment technology and equipment; Floor space is less than 100 square metres, and effluent quality reaches GB18596-2001 " livestock breeding industry pollutant emission " standard-required; Special efficacy organic fertilizer production functional module: realized pig manure production fertilizer, produced the fertilizer steady quality and reach NY525-2002 " organic fertilizer standard "; Produce natural pond electricity generate function module: produce natural pond power generation system floor space and be merely 1/3 of conventional processes; Daily output natural pond amount can reach more than 350 cubic metres; Electrogenesis potential reaches more than the 650 degree/skies, more than the extraction of natural pond liquid struvite crystallization 50Kg, can realize significant environment, society and economy benefit.
The invention has the advantages that: biological treatment process is set and a series of resource recovery measure is harmonious, realizes the zero discharge treatment of pig manure, improved the Working environment and the surrounding enviroment on pig farm greatly, be beneficial to the environment protection and the comprehensive regulation of place; Whole flow process has good integration; Can be combined to integral device; Also but modularization is divided into water purifying function module and special efficacy organic fertilizer production functional module in product natural pond power generation system functional module, the high density pig farm sewage; Whole facility floor space is little, and investment and running cost are lower, are easy to the equipmentization that realizes; The production of biogas, generating, fertilizer and struvite is organically combined, have good social benefit and economic benefit.
Most preferred embodiment of the present invention is illustrated, and various variations or the remodeling made by those of ordinary skills can not depart from the scope of the present invention.
Claims (1)
1. a pig manure material focuses on and utilization of resources method, includes pre-treatment step: the pig manure material is poured in the manure lagoon (1), and carry out the preliminary adjusting of water ratio; It is characterized in that: also include following steps:
The squeezing treatment step: the pig manure material in the manure lagoon (1) is delivered in the press apparatus (4) through lift pump (2), transport pipe (3), and the pig manure material is handled through squeezing, liquid excrement slurry;
Biogas produces step: the liquid excrement slurry after squeezing is handled gets into the excrement slurry and produces natural pond equipment (5), produces the production that natural pond equipment (5) is realized biogas by the excrement slurry;
The marsh gas purifying step: excrement slurry produce that natural pond equipment (5) produced biogas get in the marsh gas purifying equipment (7) through pneumatic tube (6), and the biogas of input is carried out purifying treatment;
The marsh gas power generation step: the biogas after the purifying treatment inputs in the biogas generator (9) after gas-holder (8) regulating, and biogas generator (9) is launched and generated electricity;
Natural pond liquid separating step: the excrement slurry produces and is left that natural pond liquid thing is arranged after natural pond equipment (5) produces the natural pond, and this natural pond liquid thing inputs to solid-liquid separating equipment (10), and isolates the excrement slag of solid attitude and the pending liquid of liquid state; The excrement slag of solid attitude is directly fallen in high temperature aerobic composting facility (13);
Struvite crystallisation step: in the isolating pending liquid input struvite crystalline element of solid-liquid separating equipment (10) institute (11), add magnesia mixture, extract and obtain the struvite crystallization; And pending liquid also produces after the struvite crystallization has residual liquid, and nitrogen element and phosphoric in this residual liquid are extracted;
The residual solution treatment step: remaining residual liquid is sprayed in the high temperature aerobic composting facility (13) through shower (14) in the struvite crystalline element (11); After the residual liquid reuse, still have remainder water liquid, it gets in the unit for treating water (12), carries out processing up to standard;
The compost treatment step: the bottom of high temperature aerobic composting facility (13) is a fermentation bed, and the excrement slag of output all is piled up on this fermentation bed in the solid-liquid separating equipment (10), and controls the aerobic fermentation of excrement slag by fermentation bed; High temperature aerobic composting facility (13) also disposes temperature control system (16) and gas blower (17), and the real time temperature of temperature control system (16) monitor fermentation bed, and the water spray of shower (14) and the air quantity of gas blower (17) are carried out feedback control;
In the described squeezing treatment step, the pig manure material reaches 45% to 70% through its water ratio of liquid excrement slurry that squeezing is processed into;
In the described squeezing treatment step, press apparatus (4) also can be isolated the excrement slag in treating processes, and this excrement slag is directly fallen in high temperature aerobic composting facility (13);
In the described marsh gas power generation step, biogas generator (9) generating is connected with lift pump (2), solid-liquid separating equipment (10), temperature control system (16), gas blower (17), promptly forms the EPS of internal system;
In the described residual solution treatment step, remaining residual solution also can return back in the manure lagoon (1) through return line (15) in the struvite crystalline element (11).
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| CN2010101355385A CN101792340B (en) | 2010-03-25 | 2010-03-25 | Pig manure centralized treatment and resource utilization method |
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| CN2010101355385A CN101792340B (en) | 2010-03-25 | 2010-03-25 | Pig manure centralized treatment and resource utilization method |
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| CN101792340B true CN101792340B (en) | 2012-09-19 |
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| CN101993182A (en) * | 2010-10-16 | 2011-03-30 | 福建洛东生物技术有限公司 | Livestock and poultry farm dung dirt biological fermentation treatment method and device |
| CN102518599B (en) * | 2011-12-08 | 2016-01-20 | 陈斌 | The vehicle-mounted pumping and spraying unit of a kind of motor-driven pulping natural pond liquid |
| CN102731179B (en) * | 2012-07-20 | 2014-02-26 | 四川四通欧美环境工程有限公司 | Treatment method of solid anaerobic and aerobic composting system for organic garbage and sludge |
| CN103588374A (en) * | 2013-11-18 | 2014-02-19 | 歙县连大生态农业科技有限公司 | Method for recycling pig manure soaking in biogas slurry to prepare methane and using pig manure comprehensively |
| CN103819053B (en) * | 2014-02-25 | 2015-08-05 | 农业部沼气科学研究所 | Struvite precipitation coupling microdisk electrode is utilized to carry out the method for natural pond liquid and marsh gas purifying |
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| CN108484232A (en) * | 2018-05-30 | 2018-09-04 | 甘肃前进牧业科技有限责任公司 | A kind of the treatment for cow manure system and processing method of dairy cow farm |
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| CN109626774A (en) * | 2018-11-20 | 2019-04-16 | 华南农业大学 | A kind of pig manure diafiltration bed produces biogas and compost integrated apparatus and its method |
| CN111592170B (en) * | 2020-07-22 | 2020-11-13 | 北京锦绣新技术发展有限公司 | Preparation method of nano magnetic material loaded mineral soil for reducing COD (chemical oxygen demand) and heavy metals in excrement, sewage and biogas slurry wastewater |
| CN111908747A (en) * | 2020-07-28 | 2020-11-10 | 山西贤美食业有限公司 | Method for environment-friendly and efficient utilization of cow dung |
| CN112759214A (en) * | 2020-12-28 | 2021-05-07 | 哈尔滨华美亿丰复合材料有限公司 | Method and system for treating feces in dairy farm |
| CN116282315B (en) * | 2023-02-20 | 2023-08-11 | 宝航环境修复有限公司 | Air floatation device for soil leaching remediation |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1060279A (en) * | 1990-09-29 | 1992-04-15 | 上海东海水产科技服务部 | Pig farm wastewater treatment and utilize technology |
| CN101070217A (en) * | 2007-06-14 | 2007-11-14 | 同济大学 | Method for increasing sewage-reinforced biological phosphor-removing effect by resource utilizing mud organic substance |
-
2010
- 2010-03-25 CN CN2010101355385A patent/CN101792340B/en not_active Expired - Fee Related
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1060279A (en) * | 1990-09-29 | 1992-04-15 | 上海东海水产科技服务部 | Pig farm wastewater treatment and utilize technology |
| CN101070217A (en) * | 2007-06-14 | 2007-11-14 | 同济大学 | Method for increasing sewage-reinforced biological phosphor-removing effect by resource utilizing mud organic substance |
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