CN106396298A - Purification device for treating poultry farming wastewater through solar bio-floating bed - Google Patents
Purification device for treating poultry farming wastewater through solar bio-floating bed Download PDFInfo
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- CN106396298A CN106396298A CN201611119009.XA CN201611119009A CN106396298A CN 106396298 A CN106396298 A CN 106396298A CN 201611119009 A CN201611119009 A CN 201611119009A CN 106396298 A CN106396298 A CN 106396298A
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- poultry farming
- kickboard
- purification device
- solar energy
- waste water
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- 239000002351 wastewater Substances 0.000 title claims abstract description 34
- 238000009374 poultry farming Methods 0.000 title claims abstract description 29
- 238000000746 purification Methods 0.000 title claims abstract description 28
- 238000007667 floating Methods 0.000 title claims abstract description 23
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 58
- 229910001868 water Inorganic materials 0.000 claims abstract description 58
- 238000005273 aeration Methods 0.000 claims abstract description 20
- 239000003610 charcoal Substances 0.000 claims abstract description 9
- 239000002131 composite material Substances 0.000 claims abstract description 9
- 239000011229 interlayer Substances 0.000 claims abstract description 9
- 239000012620 biological material Substances 0.000 claims abstract description 7
- 239000000945 filler Substances 0.000 claims abstract description 7
- 230000002786 root growth Effects 0.000 claims abstract description 4
- 241000196324 Embryophyta Species 0.000 claims description 29
- 238000000034 method Methods 0.000 claims description 28
- 230000008569 process Effects 0.000 claims description 26
- 238000005868 electrolysis reaction Methods 0.000 claims description 8
- 238000009434 installation Methods 0.000 claims description 6
- 238000006213 oxygenation reaction Methods 0.000 claims description 4
- 244000099162 Cyperus alternifolius Species 0.000 claims description 3
- 230000006978 adaptation Effects 0.000 claims description 3
- 238000002513 implantation Methods 0.000 claims description 3
- 238000001727 in vivo Methods 0.000 claims description 3
- 238000005259 measurement Methods 0.000 claims description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 20
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 11
- 238000012851 eutrophication Methods 0.000 abstract description 3
- 238000005457 optimization Methods 0.000 abstract 1
- 239000011148 porous material Substances 0.000 abstract 1
- 238000005516 engineering process Methods 0.000 description 11
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 8
- 229910052760 oxygen Inorganic materials 0.000 description 8
- 239000001301 oxygen Substances 0.000 description 8
- 244000144977 poultry Species 0.000 description 8
- 239000010865 sewage Substances 0.000 description 8
- 238000002360 preparation method Methods 0.000 description 7
- 238000006243 chemical reaction Methods 0.000 description 6
- 229910052698 phosphorus Inorganic materials 0.000 description 6
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 5
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 239000000203 mixture Substances 0.000 description 5
- 230000003647 oxidation Effects 0.000 description 5
- 238000007254 oxidation reaction Methods 0.000 description 5
- 239000011574 phosphorus Substances 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 4
- 150000001875 compounds Chemical class 0.000 description 4
- 239000008187 granular material Substances 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 241000894006 Bacteria Species 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 239000012528 membrane Substances 0.000 description 3
- 238000006396 nitration reaction Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 241000684239 Canna x generalis Species 0.000 description 2
- 229910017112 Fe—C Inorganic materials 0.000 description 2
- 241000108664 Nitrobacteria Species 0.000 description 2
- CKUAXEQHGKSLHN-UHFFFAOYSA-N [C].[N] Chemical compound [C].[N] CKUAXEQHGKSLHN-UHFFFAOYSA-N 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 238000009360 aquaculture Methods 0.000 description 2
- 244000144974 aquaculture Species 0.000 description 2
- 238000001354 calcination Methods 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 230000012010 growth Effects 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 230000001360 synchronised effect Effects 0.000 description 2
- 241000272525 Anas platyrhynchos Species 0.000 description 1
- 206010002660 Anoxia Diseases 0.000 description 1
- 241000976983 Anoxia Species 0.000 description 1
- 241000272814 Anser sp. Species 0.000 description 1
- 241000271566 Aves Species 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 229910021591 Copper(I) chloride Inorganic materials 0.000 description 1
- 206010059410 Faecaluria Diseases 0.000 description 1
- 241000238631 Hexapoda Species 0.000 description 1
- 206010021143 Hypoxia Diseases 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 1
- 230000007953 anoxia Effects 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 238000006065 biodegradation reaction Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 210000000476 body water Anatomy 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 1
- 239000012876 carrier material Substances 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- OXBLHERUFWYNTN-UHFFFAOYSA-M copper(I) chloride Chemical compound [Cu]Cl OXBLHERUFWYNTN-UHFFFAOYSA-M 0.000 description 1
- 238000013016 damping Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 239000000645 desinfectant Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000029142 excretion Effects 0.000 description 1
- 230000002550 fecal effect Effects 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- -1 high organic Substances 0.000 description 1
- 229940088597 hormone Drugs 0.000 description 1
- 239000005556 hormone Substances 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000002917 insecticide Substances 0.000 description 1
- 238000002955 isolation Methods 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 239000010936 titanium Substances 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 description 1
- 238000005406 washing 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
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F2001/46133—Electrodes characterised by the material
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/009—Apparatus with independent power supply, e.g. solar cells, windpower or fuel cells
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2203/00—Apparatus and plants for the biological treatment of water, waste water or sewage
- C02F2203/008—Mobile apparatus and plants, e.g. mounted on a vehicle
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/14—Maintenance of water treatment installations
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/302—Nitrification and denitrification treatment
-
- 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
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
-
- 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
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
-
- 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
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/20—Controlling water pollution; Waste water treatment
- Y02A20/208—Off-grid powered water treatment
- Y02A20/212—Solar-powered wastewater sewage treatment, e.g. spray evaporation
-
- 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
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Farming Of Fish And Shellfish (AREA)
- Housing For Livestock And Birds (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
Disclosed is a purification device for treating poultry farming wastewater through a solar bio-floating bed. The device comprises a plate-shaped floating body, a plurality of container bodies and a tank arranged in the middle, wherein the plate-shaped floating body comprises an upper floating plate, a lower floating plate and an interlayer, the upper floating plate is provided with a plurality of planting holes, an aquatic plant is planted into each planting hole, the lower floating plate is provided with a plurality of sieve pores, the interlayer is used for root growth of the aquatic plants, an air pump is installed at the upper end of the middle of the upper floating plate, the lower portion of an air outlet of the air pump is communicated with an air conveying pipe extending downwards, the lower end of the air conveying pipe is communicated with a plurality of aeration pipes, and the aeration pipes are used for injecting air below the plate-shaped floating body; all the container bodies are installed at the lower end of the lower floating plate, the side wall of each container body is provided with a plurality of meshes, and each container body is filled with a nitrogen removal composite biomaterial; the middle of the tank is filled with an iron-charcoal microelectrolysis purification filler. The device is used for treating water eutrophication caused by the poultry farming wastewater, and poultry farming surrounding water environment optimization and resource utilization are achieved.
Description
Technical field
The present invention relates to poultry farming water body is carried out with the field of restoration of the ecosystem process, particularly to a kind of life of solar energy
Thing floating bed processes poultry farming waste water purification device.
Background technology
In recent years, Chinese large-sized poultry farming quickly grows, and scale constantly expands.Poultry farming enterprise for a long time with
Simply to covet economic benefit, and environmental consciousness is weak, fecal sewage treatment method is fallen behind, causes substantial amounts of high concentration
Organic sewage enters in rivers and lakes, causes water quality constantly to deteriorate, and wherein the nitrogen of sewage middle and high concentration, phosphorus are to cause the rich battalion of water body
The main cause of fosterization.Most of plants do not consider poultry manure process, a large amount of fecalurias of discharge and cultivation at an initial stage of building
A large amount of waste water of field, are mostly directly discharged with process, disposal without appropriate recycling, cause serious pollution to environment,
And this waste water also can impact to the living environment of part poultry, the birdss for example some dados being perched, such as duck, goose
Deng this waste water also can impact to poultry health.
Nowadays, surrounding city poultry farming have become as or becoming suitable with industrial wastewater and sanitary sewage even
Bigger polluter.Livestock waste water, even across disposal methods such as " solid-liquid separation one anaerobism one are aerobic ", discharges
Sewage still contain compared with the pollutant such as high organic, nitrogen and phosphorus, cause the severe contamination in local environment and farmland.
Aquatic plant ecological floating bed is applied to oxidation pond and purifies water in recent years, is also used for the end of poultry farming water body
Process.Existing biologic float bed technology relies primarily on compound and the Organic substance such as plant absorption N, P of plantation in floating bed, due to being subject to
Season and the restriction of floating bed plant, for fluitante, it only utilizes surface water, and plant is limited to water body purification effect,
In the extremely low eutrophication of dissolved oxygen even in water body undergrowth, maintenance is difficult, relatively costly, and its clean-up effect is difficult to
Improve further.At present, for high nitrogen, phosphorus and organic matter, at the relatively low aquaculture water body oxidation pond of dissolved oxygen content in water body
Reason, lacks effective purification techniques.
Content of the invention
For the deficiencies in the prior art, the present invention is intended to provide a kind of solar energy is biologic float bed processes poultry farming waste water
Purifier, reaches save energy, resource, the purpose for the treatment of and purification water quality efficiency high.
For achieving the above object, the present invention adopts the following technical scheme that：
Solar energy is biologic float bed to process poultry farming waste water purification device, including：
Tabular buoyancy aid, this tabular buoyancy aid includes kickboard, lower kickboard and is located at interlayer between upper kickboard, lower kickboard,
On this, kickboard offers multiple implantation hole, and each plantation in the hole plantation has water plant, and described lower kickboard has multiple sieve apertures, should
Interlayer is used for the root growth for water plant, and on this, the middle part upper end of kickboard is provided with air pump, below the gas outlet of this air pump
The appendix that connection one extends downwardly, the lower end of described appendix connects many aeration tubes, and described aeration tube is used for floating in tabular
The lower direction injection air of body；
Multiple containers body, is mounted on the lower end of lower kickboard, the side wall of each container body thering is multiple mesh, each appearance
All placed multiple supporting bodies with gate hole, each carrying is filled with denitrogenation composite biological material in vivo in body；
It is arranged at the tank body in the middle part of tabular buoyancy aid, this tank body has comb hole, the middle part of this tank body is filled with ferrum-charcoal light electrolysis
Purify filler.
Preferably, the biologic float bed poultry farming waste water purification device that processes of described solar energy also includes a solar energy confession
Electric installation, is installed on the top of air pump, and including bracing frame, photovoltaic board component, accumulator, support frame as described above is used for photovoltaic panel group
Part provides brace foundation, and described accumulator is electrically connected at photovoltaic board component and is fixed on bracing frame, this accumulator be used for
Air pump is powered.
Preferably, the biologic float bed poultry farming waste water purification device that processes of described solar energy also includes a civil power adaptation
Electric supply installation, this civil power adaptation electric supply installation is connected by wire with outside mains supply.
Preferably, the plurality of container body is circumferentially installed on the lower end of lower kickboard in array.
Preferably, described aeration tube is porous nano oxygenation aeration pipe, the tube wall of this porous nano aeration tube has even
Logical inside and outside capillary channel.
Preferably, Canna generalis Bailey, Herba Eichhorniae, Herba penniseti, cyperus alternifolius or Herba Apii graveolentis, cultivation on tabular buoyancy aid for the described water plant
Planting density is 12～20 plants/m2.
Preferably, on this, kickboard periphery upper measurement is provided with for avoiding kickboard on this to be immersed in the water wing of the water surface, described water wing
Inner hollow, and this water wing has elasticity.
Compared to prior art, the present invention is had advantageous effect in that：
1. utilize solar energy to produce electric energy and drive air pump work it is not necessary to consume external power supply electric energy, can be effectively save
The energy, applied widely；
2. under conditions of the aeration aerating of air pump, increased oxygen in water concentration, biodegradation is played with promotion and makees
With effectively reducing pollutional load, efficiently going the Organic substances such as COD in eliminating water, nitrogen, phosphorus and other pollutant, purifying water body water quality；
3. denitrogenation compound bio carrier material, under ferrum charcoal aerobic condition, ammonia oxidation bacteria and nitrobacteria will be fast for ammonia nitrogen in water
Speed nitrification, realizes synchronous nitration and denitrification fast deep denitrogenation, is that to integrate technology of biological membrane, itself chemical reaction technology former
Bit depth denitrogenation technology.
4. pair water environment carries out three-dimensional reparation.Plant on tabular buoyancy aid and be implanted with water plant, and under water be provided with filling
The multiple containers body of denitrogenation composite biological packing supporting body, three forms biological floating bed, carries out multi-level improvement to water body,
Comprehensive fast purification water quality, substantially increases pollution control efficiency.The end-o f-pipe -control of poultry farming waste water plays and makees very well
With with applications well prospect.
5. swim in pond face so that the improvement blind area of the whole water surface is reduced.
6. in the present invention institute's growth and maturity plant can scene ground as poultry diatery supplement, and this plant can draw
Play Some Insects breeding, consequently, it is possible to poultry can easily prey on insecticide, both enriched the food species of poultry, and subtracted again
Lack the feeding volume of man-made feeds.
Brief description
Fig. 1 is the structural representation of the present invention；
Fig. 2 is the cross section view at Figure 1A-A place；
Fig. 3 is the top view of the present invention；
Wherein, 1, photovoltaic board component；2nd, bracing frame；3rd, accumulator；4th, air pump；5th, water plant；6th, tabular buoyancy aid；7th, take off
Nitrogen composite biological material；8th, appendix；9th, container body；10th, aeration tube；11st, tank body.
Specific embodiment
Below, in conjunction with accompanying drawing and specific embodiment, the present invention is described further：
As shown in Figure 1-Figure 3, solar energy is biologic float bed processes poultry farming waste water purification device, including：Tabular buoyancy aid
6th, container body 9 and tank body 11.
This tabular buoyancy aid 6 includes kickboard, lower kickboard and is located at interlayer between upper kickboard, lower kickboard, kickboard on this
Offer multiple implantation hole, each plantation in the hole plantation has water plant 5, and described lower kickboard has multiple sieve apertures, and this interlayer is used
In the root growth for water plant 5, on this, the middle part upper end of kickboard is provided with air pump 4, connects below the gas outlet of this air pump 4
The appendix 8 that one extends downwardly, the lower end of described appendix connects many aeration tubes 10, and described aeration tube 10 is used for floating in tabular
The lower direction injection air of body, the micro air bubble that described sieve aperture is used for being formed for air enters in interlayer；
The quantity of container body 9 is multiple, is mounted on the lower end of lower kickboard, the side wall of each container body thering is multiple nets
Hole, all placed multiple supporting bodies with gate hole in each container body 9, and each carrying is filled with denitrogenation composite biological material in vivo
7；
Described tank body 11 is arranged at the middle part of tabular buoyancy aid 6 and is immersed in water, and this tank body 11 has comb hole, this tank body 11
Middle part be filled with ferrum-charcoal light electrolysis and purify filler.
The supporting body with denitrogenation composite biological material 7 can achieve that under the conditions of aerobic, low C/N ratio polluted-water quickly takes off
Nitrogen, belongs to and integrates technology of biological membrane, itself chemical reaction technology advanced nitrogen technology.
It is to be with reference to notification number that ferrum of the present invention-charcoal light electrolysis purify filler composition and preparation method：
CN104150568B, entitled《A kind of catalysis and micro-electrolysis material and preparation method thereof》The content described in patent of invention carry out
Preparation：Particle diameter is less than the iron powder that 40 mesh, percentage by weight are 65～85%, particle diameter is less than 80 mesh, percentage by weight be 7～
25% graphite powder, the manganese dioxide that particle diameter is less than 100 mesh, percentage by weight is 3～10%, particle diameter is less than 120 mesh, weight hundred
Divide than the catalyst CuCl for 0.01～0.09%2Uniformly mix, add water and mixture is put into comminutor cause granular material,
Naturally by granular material isolation air in 900 DEG C～1200 DEG C temperature calcination 120 minutes, prepared catalysis and micro-electrolysis material after drying
Material.
The raw material composition of denitrogenation composite biological material of the present invention and preparation method are to be with reference to notification number
CN103145234B, entitled《Direct denitrification organisms particulate vector of aerobic low carbon-nitrogen ratio sewage ammonia nitrogen and preparation method thereof》Send out
Bright patent described content is prepared：Account for 40～50% for fe by volume, active carbon powder accounts for 35～42%, Gypsum Fibrosum
Powder accounts for 5～8%, and copper powder accounts for 4～5%, and manganese powder accounts for 1～2%, and titanium valve accounts for 1～2%, and magnesium powder accounts for 1～2%, and vanadium powder accounts for 1～2%.
Its preparation method is by material composition feeding mixing, makes the granule of 5～20mm, is dried and then at 500 DEG C～950 DEG C
Temperature calcination 90 minutes, after natural cooling, the granule of preparation is cultivated by microorganism colonization in sewage obtain aerobic low
Carbon-nitrogen ratio sewage ammonia nitrogen direct denitrification organisms particulate vector.
In order to be powered using solar energy, as a kind of preferred scheme, the biologic float bed process poultry of described solar energy
Aquaculture waste water purification device also includes solar power supply apparatus, is installed on the top of air pump, including bracing frame 2, photovoltaic
Board component 1, accumulator 3, support frame as described above 2 is used for providing brace foundation to photovoltaic board component 1, and described accumulator 3 is electrically connected with
In photovoltaic board component 1 and be fixed on bracing frame 2, this accumulator 3 is used for powering to air pump 4.
In order to the present invention also can be normally used in rainy day and night, as a kind of preferred scheme, this solar energy is given birth to
Thing floating bed processes poultry farming waste water purification device and also includes standby city electrical connection system, and this system includes wire and civil power is fitted
Join electric supply installation.Therefore, air pump 4 is round-the-clock starts, to oxidation pond or pond aeration aerating.Make waste water purification device higher efficiency
Ground runs.
As a kind of preferred scheme, the plurality of container body 9 is circumferentially installed on the lower end of lower kickboard in array.
As a kind of preferred scheme, described aeration tube 10 is porous nano oxygenation aeration pipe, this porous nano aeration tube
Tube wall on there is the inside and outside capillary channel of connection.This capillary channel has and limits the damping gushed of air-flow so that air
Enter in water in fine gas bubbles shape, and, such bubble can form slow flowing so that water body has more fully time dissolving
Oxygen.And the slow flowing of this bubble formation also can allow the surface that ferrum-charcoal light electrolysis purify filler obtain washing away of appropriateness, reduces
The situation that ferrum-charcoal light electrolysis purification filler has been used long and can be passivated occurs.
As a kind of preferred scheme, Canna generalis Bailey, Herba Eichhorniae, Herba penniseti, cyperus alternifolius or Herba Apii graveolentis, above water plant is permissible
It is to be selected in the way of selecting one/several combinations/full choosing combination, plantation density on tabular buoyancy aid for the described water plant 5 is 12
～20 plants/m2.This data is known by inventor's practice, it is to avoid influence each other between plant growth, by the absorption of single plant
Effect performs to most preferably.
As a kind of preferred scheme, on this, kickboard periphery upper measurement is provided with for avoiding kickboard on this to be immersed in the floating of the water surface
Circle, described water wing inner hollow, and this water wing has elasticity, it is to avoid and the present invention can produce just in the water surface random collision when using
Property stress upper kickboard is caused damage situation occur.
Solar energy of the present invention is biologic float bed to process poultry farming waste water purification device cleaning principle：The present invention fills
The air pump using solar energy drive oxygen processed, oxygenation is divided to be the biological floating bed dissolved oxygen ability strengthening whole system, for denitrogenation under water
The growth of microorganism of composite biological packing provides sufficient oxygen, and increases the content of Dissolved Oxygen in Water, prevent water plant because
Anoxia and lead to rot, and then clean-up effect of increasing water quality.Biological floating bed upper growing plant absorbs and removes nitrogen in eliminating water, phosphorus etc.
Nutrient, suppresses algal grown, eliminates body eutrophication, improves water transparency and serves water purification.Denitrogenation
Ammonia nitrogen in water is quickly nitrified, simultaneously in biomembrane by compound bio carrier ammonia oxidation bacteria and nitrobacteria under ferrum charcoal aerobic condition
Portion's denitrifying bacterium utilizes nascent state [H] and [Fe of Fe-C itself chemical reaction generation2+] provide electronics for anti-nitration reaction, realize
Synchronous nitration and denitrification fast deep denitrogenation；In course of reaction, Fe-C itself chemical reaction provides electronics for denitrification, significantly subtracts
Lack the carbon source consumption of denitrification process.It is therefore not necessary to additional carbon, can achieve polluted-water under the conditions of aerobic, low C/N ratio
Fast denitrogenation, is to integrate technology of biological membrane, itself chemical reaction technology advanced nitrogen technology.
Especially, common sanitary wastewater contains the impurity such as hormone, disinfectant, and herding waste water viscosity is high, containing a large amount of knots
Block residue.Process sanitary wastewater and the mode of animal husbandry waste water can not be optionally applied to poultry farming.Because processing
The mode of sanitary wastewater has and processes the attribute that time-consuming, step is many, external influence factors are more.And, containing poultry excretion
The compound of the waste water of thing, N element and P element can be more, and plant selected by the present invention is all intended to hobby and absorbs aforementioned chemical combination
The plant of thing.
It will be apparent to those skilled in the art that can technical scheme as described above and design, make other various
Corresponding change and deformation, and all these change and deformation all should belong to the protection domain of the claims in the present invention
Within.
Claims (7)
1. solar energy is biologic float bed processes poultry farming waste water purification device it is characterised in that including：
Tabular buoyancy aid, this tabular buoyancy aid includes kickboard, lower kickboard and is located at interlayer between upper kickboard, lower kickboard, on this
Kickboard offers multiple implantation hole, and each plantation in the hole plantation has water plant, and described lower kickboard has multiple sieve apertures, this interlayer
For the root growth for water plant, on this, the middle part upper end of kickboard is provided with air pump, connects below the gas outlet of this air pump
One appendix extending downwardly, the lower end of described appendix connects many aeration tubes, and described aeration tube is used in tabular buoyancy aid
Air is injected in lower direction；
Multiple containers body, is mounted on the lower end of lower kickboard, the side wall of each container body thering is multiple mesh, each container body
Inside all placed multiple supporting bodies with gate hole, each carrying is filled with denitrogenation composite biological material in vivo；
It is arranged at the tank body in the middle part of tabular buoyancy aid, this tank body has comb hole, the middle part of this tank body is filled with ferrum-charcoal light electrolysis and purifies
Filler.
2. solar energy as claimed in claim 1 biologic float bed process poultry farming waste water purification device it is characterised in that：Institute
State the biologic float bed poultry farming waste water purification device that processes of solar energy and also include solar power supply apparatus, be installed on air pump
Top, including bracing frame, photovoltaic board component, accumulator, support frame as described above is used for providing brace foundation, institute to photovoltaic board component
State accumulator to be electrically connected at photovoltaic board component and be fixed on bracing frame, this accumulator is used for powering to air pump.
3. solar energy as claimed in claim 1 biologic float bed process poultry farming waste water purification device it is characterised in that：Institute
State the biologic float bed poultry farming waste water purification device that processes of solar energy and also include a civil power adaptation electric supply installation, this civil power is fitted
Join electric supply installation to be connected by wire with outside mains supply.
4. solar energy as claimed in claim 1 biologic float bed process poultry farming waste water purification device it is characterised in that：Institute
State the lower end that multiple containers body is circumferentially installed on lower kickboard in array.
5. solar energy as claimed in claim 1 biologic float bed process poultry farming waste water purification device it is characterised in that：Institute
Stating aeration tube is porous nano oxygenation aeration pipe, and the tube wall of this porous nano aeration tube has the inside and outside capillary channel of connection.
6. solar energy as claimed in claim 1 biologic float bed process poultry farming waste water purification device it is characterised in that：Beautiful
People any of several broadleaf plants, Herba Eichhorniae, Herba penniseti, cyperus alternifolius or Herba Apii graveolentis, plantation density on tabular buoyancy aid for the described water plant be 12～20 plants/
m2.
7. solar energy as claimed in claim 1 biologic float bed process poultry farming waste water purification device it is characterised in that：Should
Upper kickboard periphery upper measurement is provided with the water wing for avoiding kickboard on this to be immersed in the water surface, described water wing inner hollow, and this is floating
Circle has elasticity.
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| CN107473389A (en) * | 2017-09-01 | 2017-12-15 | 北京科技大学 | Couple microorganism and light electrolysis combination floating bed device and the method for handling sanitary sewage |
| CN108218114A (en) * | 2017-12-29 | 2018-06-29 | 广州市环境保护工程设计院有限公司 | A kind of Inner electrolysis couples ecological floating island system |
| CN108545896A (en) * | 2018-06-25 | 2018-09-18 | 夏庆 | A kind of removable livestock and poultry cultivating wastewater purification device |
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Application publication date: 20170215 |