CN107381805A - One kind cultivation excrement dirt reutilization system - Google Patents
One kind cultivation excrement dirt reutilization system Download PDFInfo
- Publication number
- CN107381805A CN107381805A CN201710723677.1A CN201710723677A CN107381805A CN 107381805 A CN107381805 A CN 107381805A CN 201710723677 A CN201710723677 A CN 201710723677A CN 107381805 A CN107381805 A CN 107381805A
- Authority
- CN
- China
- Prior art keywords
- biogas
- excrement dirt
- reutilization system
- anaerobic reactors
- cstr anaerobic
- 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
- 238000002156 mixing Methods 0.000 claims abstract description 14
- 238000002360 preparation method Methods 0.000 claims abstract description 11
- 238000003860 storage Methods 0.000 claims abstract description 10
- 239000007788 liquid Substances 0.000 claims abstract description 9
- 230000007062 hydrolysis Effects 0.000 claims abstract description 8
- 238000006460 hydrolysis reaction Methods 0.000 claims abstract description 8
- 230000020477 pH reduction Effects 0.000 claims abstract description 8
- 239000002002 slurry Substances 0.000 claims abstract description 7
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims description 10
- 230000003009 desulfurizing effect Effects 0.000 claims description 3
- 238000010992 reflux Methods 0.000 claims description 3
- 239000000446 fuel Substances 0.000 abstract description 6
- 244000144972 livestock Species 0.000 abstract description 6
- 244000144977 poultry Species 0.000 abstract description 6
- 239000002699 waste material Substances 0.000 abstract description 6
- 239000003337 fertilizer Substances 0.000 abstract description 4
- 238000004519 manufacturing process Methods 0.000 abstract description 4
- 210000002700 urine Anatomy 0.000 abstract description 4
- 201000010099 disease Diseases 0.000 abstract description 3
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 abstract description 3
- 230000007613 environmental effect Effects 0.000 abstract description 3
- 230000001172 regenerating effect Effects 0.000 abstract description 3
- 239000007787 solid Substances 0.000 description 17
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 11
- 239000010410 layer Substances 0.000 description 7
- 229910000831 Steel Inorganic materials 0.000 description 5
- 239000010959 steel Substances 0.000 description 5
- 244000005700 microbiome Species 0.000 description 4
- 239000005416 organic matter Substances 0.000 description 3
- 239000000725 suspension Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000005611 electricity Effects 0.000 description 2
- 238000004134 energy conservation Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000002893 slag Substances 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- 208000035473 Communicable disease Diseases 0.000 description 1
- 102000002322 Egg Proteins Human genes 0.000 description 1
- 108010000912 Egg Proteins Proteins 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 241000282898 Sus scrofa Species 0.000 description 1
- 241000216843 Ursus arctos horribilis Species 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000010923 batch production Methods 0.000 description 1
- 230000000903 blocking effect Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000009313 farming Methods 0.000 description 1
- 230000002550 fecal effect Effects 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 230000004151 fermentation Effects 0.000 description 1
- 239000003205 fragrance Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 208000015181 infectious disease Diseases 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 235000013622 meat product Nutrition 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000008239 natural water Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 210000004681 ovum Anatomy 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000003071 parasitic effect Effects 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000000384 rearing effect Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000002344 surface layer Substances 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
Classifications
-
- 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
- C02F3/28—Anaerobic digestion processes
- C02F3/286—Anaerobic digestion processes including two or more steps
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
- C02F11/04—Anaerobic treatment; Production of methane by such processes
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
- C05F3/06—Apparatus for the manufacture
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L3/00—Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
- C10L3/06—Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
- C10L3/10—Working-up natural gas or synthetic natural gas
- C10L3/101—Removal of contaminants
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L3/00—Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
- C10L3/06—Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
- C10L3/10—Working-up natural gas or synthetic natural gas
- C10L3/101—Removal of contaminants
- C10L3/102—Removal of contaminants of acid contaminants
- C10L3/103—Sulfur containing contaminants
-
- 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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- 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
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/133—Renewable energy sources, e.g. sunlight
-
- 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
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Health & Medical Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Biodiversity & Conservation Biology (AREA)
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
Abstract
The invention discloses one kind cultivate excrement dirt reutilization system, including be sequentially communicated mixing preparation pond, hydrolysis acidification pool, the mixing preparation pond connects with excrement dirt source;The hydrolysis acidification pool is connected by elevator pump with CSTR anaerobic reactors;The CSTR anaerobic reactors are connected with biogas residue-biogas liquid pool;The CSTR anaerobic reactors are also communicated with wet storage holder.Cultivation excrement dirt reutilization system provided by the invention utilizes livestock and poultry cultivation excrement and urine waste production biogas, not only can be with pollution abatement, and a large amount of regenerative resource-biogas can be obtained, it can be used as fertilizer with caused biogas residue, biogas slurry, and the biogas that the fuel used in technical solution of the present invention produces for system itself, without extra fuel.Be advantageous to plant's energy-saving and emission-reduction and comprehensive utilization of resources, and can be with pollution administration, condition of improving environmental sanitation, reduce disease incident.
Description
Technical field
The present invention relates to cultivation night soil-treatment field, more particularly to a kind of cultivation excrement dirt reutilization system.
Background technology
As urbanization, industrialized constantly propulsion, cities and towns and industrial population are continuously increased, city meat product supply pressure
It is increasing, promote China's livestock breeding industry to develop towards scale, intensive direction.The farming industry life of this batch production
It is dirty that substantial amounts of excrement can be produced during production, if excrement dirt is without any processing directly discharge, farmland and stream are entered by overland flow,
Small watershed water body environment will be polluted, and cause to close on water body ammonia nitrogen and organic matter severe overweight, fecal sewage to water body and
The pollution of soil is mainly to be endangered caused by organic pollution and nitrogen, phosphorus nutrition material.Into after natural water body, make water first
Matter is muddy, and water colour turns yellow, breath malodor.Under microbial action, a large amount of dissolved oxygens (DO) consumed in water body are molten when serious
Solution oxygen is depleted, and organic matter carries out anaerobic digestion, produces various odorants, water body blackening is smelly, water quality deterioration, excrement and urine waste
And its water body, feed and the air polluted, the sprawling and development of livestock and poultry infectious disease and parasitic ovum are eventually resulted in, influences domestic animal
Poultry and human health, continuing, developing in a healthy way for scale livestock rearing industry itself is also threaten, the vicious circle of this pollution is given
The development of poultry industry causes serious harm.
The content of the invention
It is an object of the invention to:A kind of cultivation excrement dirt reutilization system is proposed, is given birth to using livestock and poultry cultivation excrement and urine waste
Biogas is produced, not only can be with pollution abatement, and a large amount of regenerative resources can be obtained --- biogas, be advantageous to plant's energy-conservation and subtract
Row and comprehensive utilization of resources, and can be with pollution administration, condition of improving environmental sanitation, reduce disease incident.
One kind cultivation excrement dirt reutilization system, including be sequentially communicated mixing preparation pond, hydrolysis acidification pool, it is described mixing adjust
Connected with pond with excrement dirt source;The hydrolysis acidification pool is connected by elevator pump with CSTR anaerobic reactors;The CSTR anaerobism
Reactor is connected with biogas residue-biogas liquid pool;The CSTR anaerobic reactors are also communicated with wet storage holder.Produced to improve biogas
Rate, temperature is preferably kept in 20 DEG C~35 DEG C in CSTR anaerobic reactors.
Preferably, the biogas residue-biogas liquid pool is communicated to mixing preparation pond by biogas slurry reflux pump.Containing big in piggery wastewater
The suspended material such as residual feed and feed package thing residue is measured, and these suspensions are easy to cause equipment and line clogging, such as
Handle not in time, may finally cause whole processing system can not normal work.To solve this problem, in the excrement dirt source with mixing
It is also associated with being provided with grid machine in grid canal grid canal between conjunction preparing pool.So that swine manure wastewater is first discharged into grid canal,
Substantial amounts of suspension is got rid of by grid maker, then enters back into mixing preparation pond.
For ease of further being used caused biogas, between the CSTR anaerobic reactors and wet storage holder
Also it is sequentially communicated moisture trap and desulfurizing tower.Caused biogas passes through moisture trap, after desulfurizing tower purified treatment, is stored in
In wet storage holder, for supplying and generating electricity.
The biogas that the fuel that the system uses produces for system itself, without extra fuel.Utilize the waste heat of marsh gas power generation
Available for heating CSTR anaerobic reactors.The CSTR anaerobic reactors can be connected methane boiler.Methane boiler can be used as standby
With heat resource equipment and emergent burner.
Biogas to be produced using the system is generated electricity, and the wet storage holder can be connected with generating set.
The CSTR anaerobic reactors that the system uses are a kind of new special to handle the larger reaction of solid contents
Device, its construction features are that three phase separator and other components are not set in reactor.Containing high organic solid content (being more than 5%)
Waste liquid is entered by bottom of pond water distribution system, is evenly distributed in the bottom of reactor, and then upper up-flow is by containing high concentration anaerobism
The Solid Bed of microorganism.Make organic solid in waste liquid and the abundant haptoreaction of anaerobe, organic solid is liquefied fermentation
And anaerobic digestion, the organic matter that there are about 50% or so are converted into biogas.And caused biogas has stirring mixed with current rising
Cooperation is used, and promotes contact of the solid with microorganism.Because there is a natural sedimentation effect in Action of Gravity Field Solid Bed area, proportion is larger
Solids (including microorganism, undegradable solid and inoganic solids etc.) is accumulated in Solid Bed bottom, makes to keep in reactor
Higher amount of solid and biomass, reactor can be made to have longer microorganism and solid retention time.Pass through the current of Solid Bed
Outside Chi Ding outlet canal overflow to pond.Slag trap is set before water outlet overflow canal, the loss of suspension in pond can be reduced, anti-
Device liquid level is answered to form one layer of scum layer, in running steady in a long-term, scum layer tends to be dynamically flat after reaching certain thickness
Weighing apparatus.Constantly there is solid to be carried to scum layer by biogas, while also there is degassed solid to return to Solid Bed area.Because biogas will
The collection chamber of reactor head is entered through scum layer, certain " broken " effect is produced to scum layer.It is anti-for productivity
Answering device, scum layer will not cause blocking because scum silica frost surface layer is larger.Biogas in collection chamber is drawn through conduit to be entered outside pond
Biogas storage cabinet.Reaction tank set discharge pipeline can by unnecessary sludge and under sink to the inert substance of bottom and periodically exclude.
Biogas residue caused by the system can be used as Raw material processing production organic fertilizer.Biogas slurry can be used for applying fertilizer or making fertilizer.
Cultivation excrement dirt reutilization system provided by the invention can not only be subtracted using livestock and poultry cultivation excrement and urine waste production biogas
Light pollution, and a large amount of regenerative resource-biogas can be obtained, it can be used as fertilizer, and this with caused biogas residue, biogas slurry
The biogas that the fuel used in inventive technique scheme produces for system itself, without extra fuel.Be advantageous to plant's energy-conservation to subtract
Row and comprehensive utilization of resources, and can be with pollution administration, condition of improving environmental sanitation, reduce disease incident.
Brief description of the drawings
Fig. 1 is the flow chart of the cultivation excrement dirt reutilization system arrangement of the present invention.
Embodiment
Below in conjunction with accompanying drawing, the technical scheme in the embodiment of the present invention is clearly and completely described, it is clear that institute
The embodiment of description is only part of the embodiment of the present invention, rather than whole embodiments.
One kind cultivation excrement dirt reutilization system, the brick mix structure grid that excrement dirt source connection size is 10.0m × 0.9m × 1.0m
Lattice canal.It is 900mm × 1000mm that specification is provided with grid canal, and grizzly bar spacing is 10mm steel grid machine.Grid canal connects
To the mixing preparation pond for the underground type steel and concrete structure that size is 4.0m × 4.0m × 3.0m.It is Ф that mixing preparation pond, which is communicated to size,
The hydrolysis acidification pool of 4.0 × 3.5m underground type steel and concrete structure.Hydrolysis acidification pool is communicated to the ground that size is Ф 10.6m × 9.6m
The CSTR anaerobic reactors of above formula steel construction, temperature is maintained at 35 DEG C in CSTR anaerobic reactors.CSTR anaerobic reactors connect
To the biogas residue-biogas liquid pool for the underground type steel and concrete structure that size is 14m × 30m × 2.8m, slag biogas slurry pond is connected by biogas slurry reflux pump
To mixing preparation pond.It is 0.15m that CSTR anaerobic reactors, which are also sequentially communicated to dischargeable capacity,3Moisture trap, dischargeable capacity
For 2.5m3Desulfurizing tower and dischargeable capacity 300m3Wet storage holder.CSTR anaerobic reactors are also communicated with methane boiler.Wet type
Air accumulator is connected with generating set.
Claims (6)
1. one kind cultivation excrement dirt reutilization system, including be sequentially communicated mixing preparation pond, hydrolysis acidification pool, it is characterised in that:
The mixing preparation pond connects with excrement dirt source;The hydrolysis acidification pool is connected by elevator pump with CSTR anaerobic reactors;Institute
CSTR anaerobic reactors are stated with biogas residue-biogas liquid pool to be connected;The CSTR anaerobic reactors are also communicated with wet storage holder.
A kind of 2. cultivation excrement dirt reutilization system according to claim 1, it is characterised in that:The biogas residue-biogas liquid pool passes through
Biogas slurry reflux pump is communicated to mixing preparation pond.
A kind of 3. cultivation excrement dirt reutilization system according to claim 1, it is characterised in that:Adjusted with mixing in the excrement dirt source
With grid canal is also associated between pond, grid machine is provided with grid canal.
A kind of 4. cultivation excrement dirt reutilization system according to claim 1, it is characterised in that:The CSTR anaerobic reactors
Moisture trap and desulfurizing tower are also sequentially communicated between wet storage holder.
A kind of 5. cultivation excrement dirt reutilization system according to claim 1, it is characterised in that:The CSTR anaerobic reactors
Also connect methane boiler.
A kind of 6. cultivation excrement dirt reutilization system according to claim 1, it is characterised in that:The wet storage holder and hair
Group of motors is connected.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710723677.1A CN107381805A (en) | 2017-08-22 | 2017-08-22 | One kind cultivation excrement dirt reutilization system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710723677.1A CN107381805A (en) | 2017-08-22 | 2017-08-22 | One kind cultivation excrement dirt reutilization system |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107381805A true CN107381805A (en) | 2017-11-24 |
Family
ID=60353580
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710723677.1A Pending CN107381805A (en) | 2017-08-22 | 2017-08-22 | One kind cultivation excrement dirt reutilization system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107381805A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108726826A (en) * | 2018-06-01 | 2018-11-02 | 四川雪宝乳业集团有限公司 | A kind for the treatment of process of feces of livestock and poultry |
CN109516839A (en) * | 2018-12-26 | 2019-03-26 | 农业部规划设计研究院 | A kind of method of livestock and poultry cultivation liquid dung acidification storage |
CN110447342A (en) * | 2019-09-16 | 2019-11-15 | 王元华 | A kind of resource circulation utilization formula ecologic breeding recreation farm |
CN114277904A (en) * | 2022-01-21 | 2022-04-05 | 北京建筑大学 | Clean anti-freezing micro-water toilet flushing system and method for treating excrement by using same |
Citations (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102276319A (en) * | 2011-06-08 | 2011-12-14 | 同济大学 | Method for removing impurities from anaerobic fermentation raw materials in livestock and poultry excrement recycling process |
CN202081096U (en) * | 2011-03-08 | 2011-12-21 | 北京国环清华环境工程设计研究院有限公司华东分院 | System for producing methane by effectively utilizing straw fermentation |
CN102583930A (en) * | 2012-03-17 | 2012-07-18 | 山东民和生物科技有限公司 | Livestock excrement biogas generation method and livestock excrement biogas generation system |
CN102757889A (en) * | 2011-04-27 | 2012-10-31 | 中国科学院青岛生物能源与过程研究所 | Method for producing methane from kitchen waste by two continuous anaerobic fermentation steps |
CN103145308A (en) * | 2013-03-05 | 2013-06-12 | 安徽禹王养殖有限公司 | Method for producing biogas in large biogas project |
CN103951148A (en) * | 2014-04-23 | 2014-07-30 | 江苏康泰环保设备有限公司 | Farm excrement comprehensive utilization system and method |
CN104355518A (en) * | 2014-11-19 | 2015-02-18 | 黑龙江省科学院科技孵化中心 | Livestock and poultry manure anaerobic fermentation device with biogas slurry reflux pipeline |
CN104561113A (en) * | 2015-01-19 | 2015-04-29 | 青岛绿色家园环境设备有限公司 | Treating method of biogas prepared by mixed fermentation of organic wastes |
CN204661706U (en) * | 2015-04-15 | 2015-09-23 | 天紫环保投资控股有限公司 | Based on the Methane Resources treatment system of CSTR fermentation unit |
CN206173191U (en) * | 2016-11-16 | 2017-05-17 | 中国葛洲坝集团机械船舶有限公司 | Circulating anaerobic fermentation system |
CN106882981A (en) * | 2017-04-18 | 2017-06-23 | 刘军林 | A kind of aquaculture excrement is dirty to concentrate method for innocent treatment |
CN207175577U (en) * | 2017-08-22 | 2018-04-03 | 贵阳台农种养殖有限公司 | One kind cultivation excrement dirt reutilization system |
-
2017
- 2017-08-22 CN CN201710723677.1A patent/CN107381805A/en active Pending
Patent Citations (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN202081096U (en) * | 2011-03-08 | 2011-12-21 | 北京国环清华环境工程设计研究院有限公司华东分院 | System for producing methane by effectively utilizing straw fermentation |
CN102757889A (en) * | 2011-04-27 | 2012-10-31 | 中国科学院青岛生物能源与过程研究所 | Method for producing methane from kitchen waste by two continuous anaerobic fermentation steps |
CN102276319A (en) * | 2011-06-08 | 2011-12-14 | 同济大学 | Method for removing impurities from anaerobic fermentation raw materials in livestock and poultry excrement recycling process |
CN102583930A (en) * | 2012-03-17 | 2012-07-18 | 山东民和生物科技有限公司 | Livestock excrement biogas generation method and livestock excrement biogas generation system |
CN103145308A (en) * | 2013-03-05 | 2013-06-12 | 安徽禹王养殖有限公司 | Method for producing biogas in large biogas project |
CN103951148A (en) * | 2014-04-23 | 2014-07-30 | 江苏康泰环保设备有限公司 | Farm excrement comprehensive utilization system and method |
CN104355518A (en) * | 2014-11-19 | 2015-02-18 | 黑龙江省科学院科技孵化中心 | Livestock and poultry manure anaerobic fermentation device with biogas slurry reflux pipeline |
CN104561113A (en) * | 2015-01-19 | 2015-04-29 | 青岛绿色家园环境设备有限公司 | Treating method of biogas prepared by mixed fermentation of organic wastes |
CN204661706U (en) * | 2015-04-15 | 2015-09-23 | 天紫环保投资控股有限公司 | Based on the Methane Resources treatment system of CSTR fermentation unit |
CN206173191U (en) * | 2016-11-16 | 2017-05-17 | 中国葛洲坝集团机械船舶有限公司 | Circulating anaerobic fermentation system |
CN106882981A (en) * | 2017-04-18 | 2017-06-23 | 刘军林 | A kind of aquaculture excrement is dirty to concentrate method for innocent treatment |
CN207175577U (en) * | 2017-08-22 | 2018-04-03 | 贵阳台农种养殖有限公司 | One kind cultivation excrement dirt reutilization system |
Non-Patent Citations (16)
Title |
---|
季立仁等: "鸡场沼气工程设计若干问题的探讨", 《中国沼气》 * |
季立仁等: "鸡场沼气工程设计若干问题的探讨", 《中国沼气》, no. 01, 20 February 2016 (2016-02-20) * |
李子富等: "养牛场一体化沼气工程启动运行效果分析", 《农业工程技术(新能源产业)》 * |
李子富等: "养牛场一体化沼气工程启动运行效果分析", 《农业工程技术(新能源产业)》, no. 08, 25 August 2010 (2010-08-25) * |
李金平等: "兰州花庄沼气发电工程九年运行效果研究", 《中国沼气》 * |
李金平等: "兰州花庄沼气发电工程九年运行效果研究", 《中国沼气》, no. 03, 20 June 2017 (2017-06-20) * |
李金怀等: "农村生态家园沼气集中供气工程效果分析", 《现代农业科技》 * |
李金怀等: "农村生态家园沼气集中供气工程效果分析", 《现代农业科技》, no. 20, 20 October 2009 (2009-10-20) * |
潘芳伟: "厌氧生态技术在生态循环畜牧养殖的应用研究", 《科技资讯》 * |
潘芳伟: "厌氧生态技术在生态循环畜牧养殖的应用研究", 《科技资讯》, no. 12, 23 April 2013 (2013-04-23) * |
甘福丁等: "规模化畜禽养殖场沼气工程", 广西科学技术出版社, pages: 32 * |
胡纪萃等: "《废水厌氧生物处理理论与技术》", 31 May 2003, 中国建筑工业出版社, pages: 228 - 229 * |
赵由才等: "《生活垃圾处理与资源化技术手册》", 31 May 2007, 冶金工业出版社, pages: 634 - 635 * |
雷平等: "CSTR在畜禽养殖粪便沼气生产技术中的研究与应用", 《北京农业》 * |
雷平等: "CSTR在畜禽养殖粪便沼气生产技术中的研究与应用", 《北京农业》, no. 09, 25 March 2013 (2013-03-25) * |
黄婧等: "规模化养殖小区沼气发电工程效益分析――以福建莆田鸿达牧业有限公司沼气发电工程为例", 《能源与环境》, no. 06, 30 December 2014 (2014-12-30) * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108726826A (en) * | 2018-06-01 | 2018-11-02 | 四川雪宝乳业集团有限公司 | A kind for the treatment of process of feces of livestock and poultry |
CN109516839A (en) * | 2018-12-26 | 2019-03-26 | 农业部规划设计研究院 | A kind of method of livestock and poultry cultivation liquid dung acidification storage |
CN110447342A (en) * | 2019-09-16 | 2019-11-15 | 王元华 | A kind of resource circulation utilization formula ecologic breeding recreation farm |
CN114277904A (en) * | 2022-01-21 | 2022-04-05 | 北京建筑大学 | Clean anti-freezing micro-water toilet flushing system and method for treating excrement by using same |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN101759323B (en) | Treatment combined process for pig farm waste water with high nitrogen content | |
CN101709004B (en) | Method for comprehensively treating livestock waste and utilizing resource | |
CN101343133B (en) | Comprehensive treatment method for wastewater of livestock and poultry cultivation | |
CN102964149B (en) | Pollution abatement method for livestock and poultry farm | |
CN107381805A (en) | One kind cultivation excrement dirt reutilization system | |
CN105271610A (en) | Comprehensive processing process of culturing farm cow dung waste water | |
CN106565058A (en) | Stockyard sewage treatment technology | |
JP2010527762A (en) | Fermenter for producing biogas from pumpable organic materials | |
CN102910789B (en) | Marine culture water compound cyclic purification system | |
CN101817615A (en) | Anaerobic-sequencing batch biofilm reactor-artificial wetland method for treating piggery wastewater | |
CN105693045B (en) | Intelligent distributed sewage recycling system | |
CN104774751A (en) | Efficient continuous treatment system of livestock and poultry organic wastes, and treatment method thereof | |
CN103819052B (en) | A kind of animal farm wastewater Zero discharging system | |
CN102674651A (en) | Feces treatment system and feces treatment method with methane project as link | |
CN207175577U (en) | One kind cultivation excrement dirt reutilization system | |
CN102133575A (en) | Combined anaerobic pretreatment method for village-in-lake domestic sewage and organic waste | |
CN205347142U (en) | Aquaculture wastewater treatment system | |
CN105152473A (en) | Culture waste water energy self circulation disposal system and method thereof | |
CN208440534U (en) | Organic refuse treating system | |
CN205974187U (en) | Waste water integrated treating equipment raises pigs | |
CN205170492U (en) | Domestic sewage purification system of unpowered aeration | |
CN210313923U (en) | Energy-efficient breed effluent disposal system | |
CN106064870A (en) | A kind of cultivating wastewater purification device | |
CN207986983U (en) | A kind of livestock and poultry feces dope processing system based on precipitation shunting | |
CN101654688B (en) | Device for efficiently producing marsh gas |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20171124 |
|
RJ01 | Rejection of invention patent application after publication |