CN105347607B - Cattle farm sewage disposal and utilization system - Google Patents
Cattle farm sewage disposal and utilization system Download PDFInfo
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- CN105347607B CN105347607B CN201510682345.4A CN201510682345A CN105347607B CN 105347607 B CN105347607 B CN 105347607B CN 201510682345 A CN201510682345 A CN 201510682345A CN 105347607 B CN105347607 B CN 105347607B
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- cattle farm
- sump
- excrement
- utilization system
- dry cleaning
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- 239000010865 sewage Substances 0.000 title claims abstract description 55
- 241000283690 Bos taurus Species 0.000 title claims abstract description 47
- 238000000855 fermentation Methods 0.000 claims abstract description 31
- 238000005108 dry cleaning Methods 0.000 claims abstract description 28
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000002893 slag Substances 0.000 claims abstract description 11
- 239000007787 solid Substances 0.000 claims abstract description 11
- 230000004151 fermentation Effects 0.000 claims description 12
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims description 12
- 238000005273 aeration Methods 0.000 claims description 8
- 238000004659 sterilization and disinfection Methods 0.000 claims description 8
- 244000205754 Colocasia esculenta Species 0.000 claims description 7
- 235000006481 Colocasia esculenta Nutrition 0.000 claims description 7
- 241000209082 Lolium Species 0.000 claims description 7
- 239000004576 sand Substances 0.000 claims description 7
- 230000001954 sterilising effect Effects 0.000 claims description 7
- 240000008042 Zea mays Species 0.000 claims description 6
- 238000001035 drying Methods 0.000 claims description 6
- 239000002994 raw material Substances 0.000 claims description 6
- 239000011150 reinforced concrete Substances 0.000 claims description 6
- 235000001674 Agaricus brunnescens Nutrition 0.000 claims description 5
- 235000002017 Zea mays subsp mays Nutrition 0.000 claims description 5
- 239000013049 sediment Substances 0.000 claims description 4
- 239000004567 concrete Substances 0.000 claims description 3
- 239000000645 desinfectant Substances 0.000 claims description 3
- 239000012530 fluid Substances 0.000 claims description 3
- 239000011148 porous material Substances 0.000 claims description 3
- 239000010802 sludge Substances 0.000 claims description 3
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 claims description 3
- 239000006228 supernatant Substances 0.000 claims description 3
- 235000016383 Zea mays subsp huehuetenangensis Nutrition 0.000 claims description 2
- 235000009973 maize Nutrition 0.000 claims description 2
- 238000009413 insulation Methods 0.000 claims 1
- 238000004080 punching Methods 0.000 claims 1
- 238000011010 flushing procedure Methods 0.000 abstract description 8
- 239000008267 milk Substances 0.000 abstract description 4
- 210000004080 milk Anatomy 0.000 abstract description 4
- 235000013336 milk Nutrition 0.000 abstract description 4
- 239000002351 wastewater Substances 0.000 abstract description 4
- 238000004065 wastewater treatment Methods 0.000 abstract description 2
- 101100298225 Caenorhabditis elegans pot-2 gene Proteins 0.000 description 9
- 239000002699 waste material Substances 0.000 description 8
- 238000004519 manufacturing process Methods 0.000 description 6
- 238000004140 cleaning Methods 0.000 description 4
- 235000005824 Zea mays ssp. parviglumis Nutrition 0.000 description 3
- 235000005822 corn Nutrition 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 241000196324 Embryophyta Species 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 230000008021 deposition Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 210000003608 fece Anatomy 0.000 description 2
- 239000003337 fertilizer Substances 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 244000000010 microbial pathogen Species 0.000 description 2
- 239000002002 slurry Substances 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- 240000004928 Paspalum scrobiculatum Species 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 238000009360 aquaculture Methods 0.000 description 1
- 244000144974 aquaculture Species 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000003967 crop rotation Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000003973 irrigation Methods 0.000 description 1
- 230000002262 irrigation Effects 0.000 description 1
- 239000003621 irrigation water Substances 0.000 description 1
- 239000010977 jade Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 230000036642 wellbeing Effects 0.000 description 1
Classifications
-
- 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
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Landscapes
- Treatment Of Sludge (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The present invention provides a kind of processing of Novel milk cattle farm wastewater and utilization system, the cattle farm is using dry cleaning up excrement and the blowdown mode of flushing water combination；The processing system includes setting pot, sump, anaerobic fermentation pond, SBR ponds, artificial swamp and gas-holder, the sewage discharge groove of the setting pot connection cattle farm, setting pot inlet is provided with grid, sump connects setting pot by groove and exports, sewage in sump is emitted into anaerobic fermentation pond by pipeline, anaerobic fermentation pond sets exhaust pipe and drainpipe, exhaust pipe connects gas-holder, drainpipe connection SBR ponds, SBR ponds connect artificial wet land treating system by pipeline or groove, sewage after artificial wetland treatment, which is used to produce, to be irrigated or directly discharges；The processing system further includes dry cleaning up excrement processing mechanism, for handling the solid slag produced in dry cleaning up excrement and sump.Resource utilization of the present invention is high, can be water-saving to greatest extent, and wastewater treatment efficiency is excellent, good in economic efficiency.
Description
Technical field
The present invention relates to agriculture field, more particularly to a kind of cattle farm sewage disposal and utilization system.
Background technology
In recent years, the large-scale cultivation of milk cow, has formed trend, with developing rapidly for milk cow production, generates
Substantial amounts of aquaculture wastewater.The waste water of cattle farm is mainly made of excrement water, flushing water etc., and concentration is high, suspended matter is high, while sewage
Sewage, which is also presented, has the characteristics that the " three high " such as COD high, NH3-N high and pathogenic microorganism height.Processing for above-mentioned sewage is not
Huge government pressure is only brought to owner, also brings serious threat to environment.With the milk cow of 5000 scale
Exemplified by, per the one day sewage that about produce 150L of cow head, treated sewage amount is up to 750 tons day by day.
At present, most cattle farms is handled using the technology such as simple anaerobism, aerobic, on the one hand, treatment effect
Bad, cost is higher, and on the other hand, the comprehensive utilization ratio of waste material is relatively low.
The content of the invention
The technical problems to be solved by the invention are bad aiming at cattle farm wastewater treatment efficiency of the prior art, give up
The defects of comprehensive utilization ratio of gurry resource is relatively low, there is provided a kind of cattle farm sewage disposal and utilization system are above-mentioned to solve
Problem.
In order to solve the above technical problems, a kind of cattle farm sewage disposal provided by the invention and utilization system, described
The blowdown mode that cattle farm is combined using dry cleaning up excrement and flushing water；The processing and utilization system include setting pot, dirt collection
Pond, anaerobic fermentation pond, SBR ponds, artificial swamp and gas-holder, the sewage discharge groove of the setting pot connection cattle farm, heavy
Sha Chi inlet is provided with lattice, and sump connects setting pot by groove and exports, and the sewage in sump is emitted into by pipeline
In anaerobic fermentation pond, anaerobic fermentation pond sets exhaust pipe and drainpipe, exhaust pipe connection gas-holder, and drainpipe connects SBR ponds,
SBR ponds connect artificial swamp by pipeline or groove, and the sewage after artificial wetland treatment, which is used to produce, to be irrigated or directly arrange
Put；The processing and utilization system further include dry cleaning up excrement processing mechanism, for handling what is produced in dry cleaning up excrement and sump
Solid slag；The area of the artificial swamp is calculated as 2.5hm with 5000 cow head scales2, the area maize planting of wetland 80%
Or rye grass, remaining plantation taro, sewage artificial swamp demurrage in 3d.
In the above-mentioned technical solutions, it is additionally provided with sterilization pool between the SBR ponds and artificial swamp.
In the above-mentioned technical solutions, the setting pot uses reinforced concrete structure, and volume is in terms of 5000 cow head scales
For 10m3, more than available depth 1.0m, more than dwell time of sewage 1h, bottom of pond sets sand hopper, and sand hopper is taper, and bottom sets sediment outflow
Pipe.
In the above-mentioned technical solutions, the sump dischargeable capacity is 5 ~ 7 times of setting pot, using armored concrete knot
Structure, dwell time of sewage 1d.
In the above-mentioned technical solutions, the sump is provided with drainpipe, for by supernatant be discharged into anaerobic fermentation pond into
Row fermentation, is additionally provided with scum pipe, for the solid slag of deposition to be discharged, send to dry cleaning up excrement processing mechanism.
In the above-mentioned technical solutions, the anaerobic fermentation tank waterpower residence time is 5d, by more than 2 to be arranged in parallel
Marsh gas fermentation pool is formed, and using reinforced concrete structure, the volume of single marsh gas fermentation pool is 8 ~ 10 times of sump, is equipped with
Feed pipe, circulation pipe, sludge pipe and insulating layer, are stirred by the way of the zymotic fluid that flows back.
In the above-mentioned technical solutions, the SBR ponds are made of 4 ~ 6 aeration tanks being arranged in parallel, using air blast micropore
Aeration mode is aerated, and single pool volume is 5 ~ 6 times of setting pot.
In the above-mentioned technical solutions, the disinfectant of the sterilization pool selects NaClO, using intermittent drainage mode, effectively
Volume is 4 ~ 5 times of setting pot.
In the above-mentioned technical solutions, the dry cleaning up excrement processing mechanism is that dry cleaning up excrement dries mechanism, for by dry cleaning up excrement sum aggregate
The solid slag produced in dirty pond is used as planting edible mushroom raw material after drying.
Compared with prior art, the beneficial effects of the present invention are：（1）Wastewater purifying efficiency is preferable, artificial wet land system
Clean-up effect can be improved, and the effluent quality after processing is preferable, can be used as production irrigation water, improve the comprehensive utilization ratio of water,
Using water wisely；（2）Better economic benefit, the excrement slag of cattle farm and the waste residue of sump, carry out the drying process such as solarization after collection,
The cow dung dried is good planting edible mushroom raw material, and " turning waste into wealth ", certain economic benefit can be increased by selling.It is meanwhile logical
The selection plantation of constructed wetland plant is crossed, increases income, or cattle farm provides a part of greenfeed, reduces enterprise
Operating cost；（3）The utilization rate of waste resource is higher, the waste residue produced in processing procedure, and the water outlet of artificial wet land system,
Good utilization has been obtained, beneficial to environmental protection, has improved the utilization rate of waste resource.
Brief description of the drawings
Fig. 1 is the structure diagram of the present invention；
Wherein, 1- cattle farms, 2- setting pots, 3- sumps, 4- anaerobic fermentations pond, 5- SBR ponds, 6- sterilization pools,
7- artificial swamps, 8- gas-holders, 9- grids, 10- do cleaning up excrement processing mechanism.
Embodiment
The specific embodiment of the present invention is described in further detail below in conjunction with attached drawing：
As shown in Fig. 1, the cattle farm 1 of cattle farm sewage disposal and utilization system designed by the present invention is using dry
The blowdown mode that cleaning up excrement and flushing water combine.The blowdown of cattle farm 1 at present generally has three kinds of modes, does cleaning up excrement formula, flushing-water type
With bubble excrement formula, present invention selection blowdown by the way of dry cleaning up excrement and flushing water combine, on the one hand can collect dry cleaning up excrement again
Utilize, on the other hand also effectively reduce the content of excrement in sewage, difficulty is reduced for sewage disposal.
The processing and utilization system include setting pot 2, sump 3, anaerobic fermentation pond 4, SBR ponds 5, Manual moist
Ground 7 and gas-holder 8, the setting pot 2 connect the sewage discharge groove of cattle farm 1,2 inlet of setting pot are provided with lattice
Grid 9, sump 3 connect setting pot 2 by groove and export, and the sewage in sump 3 is emitted into anaerobic fermentation pond by pipeline
In 4, anaerobic fermentation pond 4 sets exhaust pipe and drainpipe, exhaust pipe connection gas-holder 8, drainpipe connection SBR ponds 5, SBR
Pond 5 connects artificial swamp 7 by pipeline or groove, and the sewage after the processing of artificial swamp 7, which is used to produce, to be irrigated or directly arrange
Put；The processing and utilization system further include dry cleaning up excrement processing mechanism 10, for handling production in dry cleaning up excrement and sump 3
Raw solid slag.
Inventor designs the sewage disposal of cattle farm and utilization system using such mentality of designing, is on the one hand
After by the way of dry cleaning up excrement and flushing water combine, the concentration of solid deposited thing can be greatly reduced in sewage, and when processing more holds
Easily, on the other hand it is then the consideration of using water wisely as far as possible and environmental protection.Can be by sewage in processing procedure using above-mentioned design
In be changed into biogas manufacture raw material and artificial swamp fertilizer, on the one hand can manufacture this clean energy resource of biogas for owner use,
On the other hand be then the mode handled using the ecosystem come treated sewage, drastically increase economic benefit.And it is entirely
The water resource of system can accomplish to recycle or recycle, and the water of artificial swamp discharge can be used for agricultural irrigation, can also follow
Ring is used as the flushing water of cattle farm 1, has accomplished the saving as far as possible of water resource.
The setting pot 2 is mainly used for removing heavier inorganic matter in sewage, mitigates fermentation vat load, avoids inorganic matter from sinking
Product occupies effective fermenting space in fermentation vat, while can also reduce fermentation vat sediment cleaning frequency.Can at 2 front entrance of setting pot
To be welded grid 9 with reinforcing bar, it is mainly used for intercepting not degradable rubbish and sedimentation silt.With the cattle farm of 5000 scales
Meter, for one day sewage load at 750 tons or so, the design dischargeable capacity of setting pot 2 is 10m3, it is preferred to use armored concrete
Structure, for available depth more than more than 1.0m, dwell time of sewage 1h, bottom of pond can set sand hopper, and sand hopper is preferably taper, bottom
If sediment outflow pipe.
The sump 3 mainly carries out secondary precipitation to the sewage of setting pot 2, and design dischargeable capacity is setting pot 2
5 ~ 7 times, using reinforced concrete structure, dwell time of sewage 1d.Sump 3 is provided with drainpipe, for supernatant to be arranged
Enter anaerobic fermentation pond 4 to ferment, scum pipe can be also set, for the solid slag of deposition to be discharged, send to the processing of dry cleaning up excrement
Mechanism 10.
4 hydraulic detention time of anaerobic fermentation pond is 5d, is made of more than 2 marsh gas fermentation pools being arranged in parallel,
Using reinforced concrete structure, the volume of single marsh gas fermentation pool is 8 ~ 10 times of sump 3, equipped with feed pipe, circulation pipe,
Sludge pipe and insulating layer, are stirred by the way of the zymotic fluid that flows back.Anaerobic fermentation pond 4 mainly utilizes sewage fermentation and biogas production,
On the one hand sewage has been handled, on the other hand can also have produced clean energy resource.
The SBR ponds 5 are made of 4 ~ 6 aeration tanks being arranged in parallel, and are aerated using air blast micro-pore aeration mode, single
Pool volume is 5 ~ 6 times of setting pot 2.Using air blast micro-pore aeration mode, SBR ponds can be controlled by adjusting aeration time
5 dissolved oxygen concentrations, make aerobic-anoxic alternately, and in favor of the removal to ammonia nitrogen, preferably 6h is a cycle of operation.
The disinfectant of the sterilization pool 6 selects NaClO, and using intermittent drainage mode, dischargeable capacity is setting pot 2
4 ~ 5 times.Sterilization pool 6 is mainly that the sewage after handling SBR ponds 5 is carried out disinfection and sterilized, and kills coliform therein
Deng pathogenic microorganisms.
The area of the artificial swamp 7 is calculated as 2.5hm with 5000 cow head scales2, the area plantation jade of wetland 80%
Rice or rye grass, remaining plantation taro, sewage artificial swamp demurrage in 3d.Inventor designs artificial swamp 7 to handle
Follow-up sewage, mainly consideration purify sewage with the ecosystem, while improving purification efficiency, moreover it is possible to obtain wholesale as far as possible
Economic well-being of workers and staff.For this reason, the corn that the fertilizer requirement of the suitable local plantation of selection is big, well developed root system, biomass are big, rye grass and
Taro, which carries out the plantation of timesharing subregion, to be advisable.The plant of corn and rye grass as the crop rotation of winter in summer, can meet cattle farm to greenfeed
Demand, biogas slurry passes through corn（Or rye grass）Ground flows into taro after coming out, milpa and taro whole furrow ditch, biogas slurry exist
Flow furrow ditch intermittent.Artificial swamp area design：By about 2.5hm2Field is divided into 3 pieces, two pieces of 1hm2Be used for plant
Corn or rye grass, remaining 0.5hm2For planting taro.
The dry cleaning up excrement processing mechanism 10 is preferably dry cleaning up excrement drying mechanism, for will be produced in dry cleaning up excrement and sump 3
Raw solid slag is used as planting edible mushroom raw material after drying.The waste residue of dry cleaning up excrement and sump 3, carries out solarization etc. after collection
Drying process, the cow dung dried are good planting edible mushroom raw materials, it " is turned waste into wealth ", can further increase warp after sale
Ji benefit.
The core of the present invention is that the blowdown mode of cattle farm is combined as using dry cleaning up excrement and flushing water, with anaerobism, aerobic
Sewage disposal is carried out to reach water-saving, the high level of resources utilization and the mesh taken into account of environmental protection with reference to the mode of artificial swamp Ecological Disposal
, therefore, protection scope of the present invention is not limited only to above-described embodiment, any using above-mentioned on the basis of the principle of the invention
The change or deformation of mechanism, belong to protection scope of the present invention.
Claims (9)
1. a kind of cattle farm sewage disposal and utilization system, it is characterised in that：The cattle farm（1）Using dry cleaning up excrement and punching
The blowdown mode that wash water combines；The processing and utilization system include setting pot（2）, sump（3）, anaerobic fermentation pond
（4）, SBR ponds（5）, artificial swamp（7）And gas-holder（8）, the setting pot（2）Connect cattle farm（1）Sewage discharge ditch
Groove, in setting pot（2）Inlet is provided with grid（9）, sump（3）Setting pot is connected by groove（2）Outlet, sump
（3）In sewage anaerobic fermentation pond is emitted into by pipeline（4）It is interior, anaerobic fermentation pond（4）Exhaust pipe and drainpipe, exhaust are set
Pipe connects gas-holder（8）, drainpipe connection SBR ponds（5）, SBR ponds（5）Artificial swamp is connected by pipeline or groove（7）, warp
Artificial swamp（7）Sewage after processing, which is used to produce, to be irrigated or directly discharges；The processing and utilization system further include dry
Cleaning up excrement processing mechanism（10）, for handling dry cleaning up excrement and sump（3）The solid slag of interior generation；The artificial swamp（7）'s
Area is calculated as 2.5hm with 5000 cow head scales2, the area maize planting of wetland 80% or rye grass, remaining plantation taro,
Sewage artificial swamp demurrage in 3d.
2. cattle farm sewage disposal and utilization system according to claim 1, it is characterised in that：The SBR ponds
（5）And artificial swamp（7）Between be additionally provided with sterilization pool（6）.
3. cattle farm sewage disposal and utilization system according to claim 1 or 2, it is characterised in that：It is described heavy
Sand pond（2）Using reinforced concrete structure, volume is calculated as 10m with 5000 cow head scales3, more than available depth 1.0m, dirt
More than water retention time 1h, bottom of pond set sand hopper, and sand hopper is taper, and bottom sets sediment outflow pipe.
4. cattle farm sewage disposal and utilization system according to claim 1 or 2, it is characterised in that：The collection
Dirty pond（3）Dischargeable capacity is setting pot（2）5 ~ 7 times, using reinforced concrete structure, dwell time of sewage 1d.
5. cattle farm sewage disposal and utilization system according to claim 4, it is characterised in that：The sump
（3）Drainpipe is provided with, for supernatant to be discharged into anaerobic fermentation pond（4）Ferment, be additionally provided with scum pipe, for that will sink
Long-pending solid slag discharge, send to dry cleaning up excrement processing mechanism（10）.
6. cattle farm sewage disposal and utilization system according to claim 1 or 2, it is characterised in that：It is described to detest
Aerobe fermentation pond（4）Hydraulic detention time is 5d, is made of more than 2 marsh gas fermentation pools being arranged in parallel, using armored concrete
Structure, the volume of single marsh gas fermentation pool is sump（3）8 ~ 10 times, equipped with feed pipe, circulation pipe, sludge pipe and insulation
Layer, is stirred by the way of the zymotic fluid that flows back.
7. cattle farm sewage disposal and utilization system according to claim 1 or 2, it is characterised in that：The SBR
Pond（5）It is made of 4 ~ 6 aeration tanks being arranged in parallel, is aerated using air blast micro-pore aeration mode, single pool volume is setting pot
（2）5 ~ 6 times.
8. cattle farm sewage disposal and utilization system according to claim 2, it is characterised in that：The sterilization pool
（6）Disinfectant select NaClO, using intermittent drainage mode, dischargeable capacity is setting pot（2）4 ~ 5 times.
9. cattle farm sewage disposal and utilization system according to claim 1, it is characterised in that：The dry cleaning up excrement
Processing mechanism（10）Mechanism is dried for dry cleaning up excrement, for by dry cleaning up excrement and sump（3）The solid slag of interior generation is made after drying
For planting edible mushroom raw material.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510682345.4A CN105347607B (en) | 2015-10-21 | 2015-10-21 | Cattle farm sewage disposal and utilization system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510682345.4A CN105347607B (en) | 2015-10-21 | 2015-10-21 | Cattle farm sewage disposal and utilization system |
Publications (2)
| Publication Number | Publication Date |
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| CN105347607A CN105347607A (en) | 2016-02-24 |
| CN105347607B true CN105347607B (en) | 2018-05-15 |
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| CN201510682345.4A Active CN105347607B (en) | 2015-10-21 | 2015-10-21 | Cattle farm sewage disposal and utilization system |
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Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107445407A (en) * | 2017-09-08 | 2017-12-08 | 常州思宇环保材料科技有限公司 | A kind of waste water treatment system for nursery and its processing method |
| CN108585388A (en) * | 2018-07-11 | 2018-09-28 | 上海环境工程设计研究院有限公司 | A kind of biogas slurry treatment device |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102515430A (en) * | 2011-12-14 | 2012-06-27 | 湖南农业大学 | Live pig slaughtering wastewater treating method |
| CN205740634U (en) * | 2015-10-21 | 2016-11-30 | 武汉现代都市农业规划设计院股份有限公司 | Novel milk cattle farm wastewater processes and utilization system |
-
2015
- 2015-10-21 CN CN201510682345.4A patent/CN105347607B/en active Active
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102515430A (en) * | 2011-12-14 | 2012-06-27 | 湖南农业大学 | Live pig slaughtering wastewater treating method |
| CN205740634U (en) * | 2015-10-21 | 2016-11-30 | 武汉现代都市农业规划设计院股份有限公司 | Novel milk cattle farm wastewater processes and utilization system |
Non-Patent Citations (1)
| Title |
|---|
| "UASB、SBR、稳定塘组合工艺处理高浓度养殖废水研究";徐耀鹏;《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑》;20120415;第15页第2-6段 * |
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