CN106698667B - A method of improving efficiency culturing pool treatment effeciency - Google Patents
A method of improving efficiency culturing pool treatment effeciency Download PDFInfo
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- CN106698667B CN106698667B CN201710007404.7A CN201710007404A CN106698667B CN 106698667 B CN106698667 B CN 106698667B CN 201710007404 A CN201710007404 A CN 201710007404A CN 106698667 B CN106698667 B CN 106698667B
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- 238000000034 method Methods 0.000 title claims abstract description 15
- 238000012258 culturing Methods 0.000 title claims abstract description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 64
- 241000251468 Actinopterygii Species 0.000 claims abstract description 14
- 238000000746 purification Methods 0.000 claims abstract description 11
- 238000009360 aquaculture Methods 0.000 claims abstract description 8
- 244000144974 aquaculture Species 0.000 claims abstract description 8
- 239000003643 water by type Substances 0.000 claims abstract description 8
- 238000005273 aeration Methods 0.000 claims abstract description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 5
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 5
- 239000001301 oxygen Substances 0.000 claims abstract description 5
- 235000013305 food Nutrition 0.000 claims abstract description 4
- 238000005192 partition Methods 0.000 claims description 6
- 235000015170 shellfish Nutrition 0.000 claims 1
- 241000195493 Cryptophyta Species 0.000 description 11
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 10
- 229910052757 nitrogen Inorganic materials 0.000 description 9
- 238000009395 breeding Methods 0.000 description 5
- 230000001488 breeding effect Effects 0.000 description 5
- 241000196324 Embryophyta Species 0.000 description 4
- 241000252234 Hypophthalmichthys nobilis Species 0.000 description 4
- 241000755266 Kathetostoma giganteum Species 0.000 description 4
- 238000013461 design Methods 0.000 description 4
- 230000000050 nutritive effect Effects 0.000 description 4
- 229910052698 phosphorus Inorganic materials 0.000 description 4
- 150000003839 salts Chemical class 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 238000006213 oxygenation reaction Methods 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- 241000169203 Eichhornia Species 0.000 description 2
- 230000007547 defect Effects 0.000 description 2
- 238000012851 eutrophication Methods 0.000 description 2
- 238000006396 nitration reaction Methods 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 230000000243 photosynthetic effect Effects 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 150000003384 small molecules Chemical class 0.000 description 2
- 230000006641 stabilisation Effects 0.000 description 2
- 238000011105 stabilization Methods 0.000 description 2
- 241001148471 unidentified anaerobic bacterium Species 0.000 description 2
- 206010020880 Hypertrophy Diseases 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 208000010824 fish disease Diseases 0.000 description 1
- 235000021060 food property Nutrition 0.000 description 1
- 238000003306 harvesting Methods 0.000 description 1
- BHEPBYXIRTUNPN-UHFFFAOYSA-N hydridophosphorus(.) (triplet) Chemical compound [PH] BHEPBYXIRTUNPN-UHFFFAOYSA-N 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- DJFBJKSMACBYBD-UHFFFAOYSA-N phosphane;hydrate Chemical compound O.P DJFBJKSMACBYBD-UHFFFAOYSA-N 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 238000009736 wetting 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
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
- C02F3/327—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae characterised by animals and plants
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G31/00—Soilless cultivation, e.g. hydroponics
- A01G31/02—Special apparatus therefor
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
- A01K63/003—Aquaria; Terraria
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
- A01K63/04—Arrangements for treating water specially adapted to receptacles for live fish
-
- 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
- C02F3/308—Biological phosphorus removal
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/105—Phosphorus compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- 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
- C02F2103/007—Contaminated open waterways, rivers, lakes or ponds
-
- 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
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/20—Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2
- Y02P60/21—Dinitrogen oxide [N2O], e.g. using aquaponics, hydroponics or efficiency measures
-
- 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
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Biodiversity & Conservation Biology (AREA)
- Engineering & Computer Science (AREA)
- Water Supply & Treatment (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Hydrology & Water Resources (AREA)
- Microbiology (AREA)
- Animal Husbandry (AREA)
- Marine Sciences & Fisheries (AREA)
- Biotechnology (AREA)
- Botany (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Farming Of Fish And Shellfish (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The present invention relates to a kind of method for improving efficiency culturing pool treatment effeciency, culture circulation system includes that the cultivation pool area of feeding fish and the purification pool area of cultivation filter food are eaten in cultivation；The drainage ditch of cultivation pool area surrounds independent region with purse seine, and hydrophyte natantia is arranged inside, and forms anaerobic zone；Two independent regions are surrounded with purse seine in purification pool area, according to Filter feeding bivalves are only arranged in first region of water (flow) direction, hydrophyte natantia is only set in Two Areas, other waters surface are to open wide the water surface, put a small amount of filter-feeding fish in a suitable place to breed；Aerobic zone --- anaerobic zone --- aerobic zone is sequentially formed in clarifier-tank；Culture circulation system provides the circulation power of water lift by the impeller being arranged at aquaculture pond and clarifier-tank handover marginal position；Impeller closes operation once every three days, closes 24 hours, increases the hydraulic detention time of purifying area, and when impeller is closed, culture zone starts spare emergency aeration oxygen replenishing.
Description
Technical field
The present invention relates to a kind of efficiency aquaculture ponds, are a kind of sides for improving efficiency culturing pool treatment effeciency specifically
Method belongs to efficiency culturing pool processing technology field.
Background technique
Efficiency pond mainly uses the breeding way of cellular-type, by filter-feeding fish and eats feeding fish and separates, to avoid
The problem of harvesting difficulty, also, the efficiency pond part water surface is purifying area, the part water surface is cultivation cement pit, to make cultivation system
It unites more efficient, it is water-saving.
Can efficiency pond play high-efficiency water-saving effect timely effectively take off cultivation discharge water depending on purifying area
Nitrogen dephosphorization reaches water circulation utilization.Purifying area is not made full use of using relatively fewer in previous design and research
Denitrification dephosphorization technique is combined with efficiency pond purifying area.Purifying area is inadequate to cultivation wastewater treatment, be easy to cause whole system
Breeding water body eutrophication, fish diseases occur.Therefore, the water treatment efficiency of efficiency aquaculture pond especially purifying area is improved to energy
The operation in effect pond becomes this field technical problem urgently to be solved.
Summary of the invention
Technical problem to be solved by the invention is to provide a kind of method of the raising water treatment efficiency of efficiency aquaculture pond, solutions
The breeding way of certainly present cellular-type is due to the not denitrogenation dephosphorization to cultivation discharge water very well, breeding water body eutrophy in system
The defect of change.
The present invention takes following technical scheme:
A method of efficiency culturing pool treatment effeciency being improved, culture circulation system includes that supporting for feeding fish is eaten in cultivation
Grow the purification pool area of pool area and cultivation filter food；The drainage ditch of the cultivation pool area surrounds independent region with purse seine,
Hydrophyte natantia is arranged inside, forms anaerobic zone；Two independent regions are surrounded with purse seine in the purification pool area, according to
Filter feeding bivalves are only arranged in first region in water (flow) direction, hydrophyte natantia are only arranged in Two Areas, other waters surface
To open wide the water surface, a small amount of filter-feeding fish is put in a suitable place to breed；Aerobic zone --- anaerobic zone --- aerobic zone is sequentially formed in clarifier-tank；
Hydrophyte natantia area coverage accounts for the 8%-12% of entire culture circulation system；The culture circulation system is being supported by setting
It grows the impeller at pond and clarifier-tank handover marginal position and the circulation power of water lift is provided；The impeller closes operation every three days
Once, it closes 24 hours, increases the hydraulic detention time of purifying area, when impeller is closed, culture zone starts spare emergency aeration
Oxygenation.
The technical program puts hydrophyte natantia in a suitable place to breed in the drainage ditch of culture zone, and water plant can cover whole in two weeks
A drainage ditch, hydrophyte natantia prevent light to enter water body, form anaerobic zone, are separated out a part of waters in purifying area,
It is separated with purse seine, puts hydrophyte natantia in a suitable place to breed, water plant can cover entire drainage ditch, hydrophyte natantia resistance in two weeks
Stopped light and entered water body, formed second anaerobic zone, other waters surface are to open wide the water surface, put in a suitable place to breed a small amount of filter-feeding fish (flathead,
Silver carp), in addition water body flow, is aerobic zone.Cultivation discharge water cultivates sludge also from sewage draining exit stream from discharge outlet from drainage ditch is flowed into
Into drainage ditch (daily tube drawing is primary), in drainage ditch anaerobic zone, macromolecular particle organic matter resolves into small molecule through anaerobic bacteria flora
Organic matter, decomposed is at Dissolve N and P nutritive salt, and then the water body of drainage ditch flows into purifying area, and purifying area aerobic zone is photosynthetic
Dissolve N and P nutritive salt is converted to algae by bacterium, and water body passes through Filter feeding bivalves, and most of algae is eaten by filter, and water body passes through
Filter-feeding fish (flathead, silver carp), a part of algae are eaten by filter again, and water body is using hydrophyte natantia area, under anaerobic environment,
Water phosphorus recycling is acted on by nitration denitrification, and a part is converted into nitrogen, and a part is absorbed by hydrophyte natantia；
And under anaerobic environment, algae is inhibited, to maintain the stabilization of algae phase.Water body is using aerobic zone oxygenation, by mentioning
Wetting system is mentioned to culture zone.
Further, the drainage system setting of the culture circulation system is divided into water circulation system in cultivation pool area
With bottom blowdown system, the bottom blowdown system is opened once daily, is opened 15 minutes every time.
Further, there is partition, first region and Two Areas mirror image among the water purification pool area
It is located at the two sides of the partition.
Further, the culture circulation system is in rectangular configuration.
The beneficial effects of the present invention are:
1) denitrogenation dephosphorization of the breeding way of present cellular-type due to not discharging water to cultivation very well is solved, is supported in system
Grow the defect of water eutrophication；
2) hydrophyte natantia is set in the drainage ditch of aquaculture pond, Filter feeding bivalves is sequentially arranged in purifying area
The second area of first area and hydrophyte natantia, to generally form anaerobic zone --- aerobic zone --- anaerobic zone ---
The water circulation of aerobic zone, it is ingenious in design, efficiency culturing pool treatment effeciency is greatly improved, algae Xiang Wending is maintained.
3) impeller closes operation once every three days, closes 24 hours, increases the hydraulic detention time of purifying area, push away
When flowing device closing, culture zone starts spare emergency aeration oxygen replenishing, ingenious in design, further improves energy-efficient effect, increases simultaneously
The efficiency of water process is added.
Detailed description of the invention
Fig. 1 is that the plane for the culture circulation system that the method that the present invention improves efficiency culturing pool treatment effeciency is based on is shown
It is intended to.
Fig. 2 is the partial enlarged view of Fig. 1.
In figure, 1. inlet channels, 2. drainage ditch, 3. aquaculture ponds, 4. closed drains, 5. discharge outlet, 6. water inlets, 7. plug-flows
Device.
Specific embodiment
Present invention will be further explained below with reference to the attached drawings and specific examples.
Referring to Fig. 1, a method of efficiency culturing pool treatment effeciency being improved, culture circulation system includes cultivation food property
The cultivation pool area of fish and the purification pool area of cultivation filter food；The drainage ditch of the cultivation pool area surrounds independence with purse seine
Region, be arranged inside hydrophyte natantia, form anaerobic zone；Two independent areas are surrounded with purse seine in the purification pool area
Hydrophyte natantia is only arranged in Two Areas according to Filter feeding bivalves are only arranged in first region of water (flow) direction in domain,
His water surface is to open wide the water surface, puts a small amount of filter-feeding fish in a suitable place to breed；Aerobic zone --- anaerobic zone --- is sequentially formed in clarifier-tank
Aerobic zone；Hydrophyte natantia area coverage accounts for the 8%-12% of entire culture circulation system；The culture circulation system relies on
Impeller at aquaculture pond and clarifier-tank handover marginal position is set, the circulation power of water lift is provided；The impeller is every three days
It is primary to close operation, closes 24 hours, increases the hydraulic detention time of purifying area, when impeller is closed, culture zone starting is spare
Emergency aeration oxygen replenishing.
The drainage system setting of the culture circulation system is divided into water circulation system and bottom blowdown system in cultivation pool area
System, the bottom blowdown system are opened once daily, are opened 15 minutes every time.
Referring to Fig. 1, there is partition, first region is set with Two Areas mirror image among the water purification pool area
In the two sides of the partition.The culture circulation system is in rectangular configuration.
Drainage ditch is anaerobic zone, Filter feeding bivalves are aerobic zone, fluitante area be anaerobic zone, cultivation discharge water successively pass through
Anaerobism, aerobic, anaerobism, aerobic several regions are crossed, achieve the purpose that denitrogenation dephosphorizing.
Fluitante selects water hyacinth kind, has higher efficiencies of nitrogen removal, with the growth of purse seine delineation water hyacinth, prevents water
Cucurbit hypertrophy influences water body dissolved oxygen.Fluitante area coverage accounts for the 10% of whole system.
The present invention puts hydrophyte natantia in a suitable place to breed in the drainage ditch of culture zone, and water plant can cover entire row in two weeks
Water channel, hydrophyte natantia prevent light to enter water body, form anaerobic zone, are separated out a part of waters in purifying area, with enclosing
Net separates, and puts hydrophyte natantia in a suitable place to breed, and water plant can cover entire drainage ditch in two weeks, and hydrophyte natantia prevents
Light enters water body, forms second anaerobic zone, other waters surface are to open wide the water surface, puts a small amount of filter-feeding fish (flathead, silver carp) in a suitable place to breed,
In addition water body flow, is aerobic zone.Cultivation discharge water also flows into row from sewage draining exit from discharge outlet from drainage ditch, cultivation sludge is flowed into
Water channel (daily tube drawing is primary), in drainage ditch anaerobic zone, it is organic that macromolecular particle organic matter through anaerobic bacteria flora resolves into small molecule
Object, decomposed is at Dissolve N and P nutritive salt, and then the water body of drainage ditch flows into purifying area, purifying area aerobic zone photosynthetic bacteria
Dissolve N and P nutritive salt is converted to algae, water body passes through Filter feeding bivalves, and most of algae is eaten by filter, and water body is eaten through filtering
Property fish (flathead, silver carp), a part of algae again by filter eat, water body is using hydrophyte natantia area, under anaerobic environment, water body
Middle nitrogen and phosphorous nutrient is acted on by nitration denitrification, and a part is converted into nitrogen, and a part is absorbed by hydrophyte natantia；And
Under anaerobic environment, algae is inhibited, to maintain the stabilization of algae phase.Water body is set using aerobic zone oxygenation by water lift
It is standby to mention to culture zone.
It is the preferred embodiment of the present invention above, those skilled in the art can carry out various change on this basis
Into or transformation, under the premise of not departing from the present invention total design, these modifications and variations are all in claimed model
Within enclosing.
Claims (4)
1. a kind of method for improving efficiency culturing pool treatment effeciency, it is characterised in that:
Culture circulation system includes that the cultivation pool area of feeding fish and the purification pool area of cultivation filter food are eaten in cultivation；
The drainage ditch of the cultivation pool area surrounds independent region with purse seine, and hydrophyte natantia is arranged inside, forms anaerobism
Area；
Two independent regions are surrounded with purse seine in the purification pool area, according to only setting is filtered in first region of water (flow) direction
Hydrophyte natantia is only arranged in Two Areas in feeding habits shellfish, other waters surface are to open wide the water surface, puts a small amount of filter-feeder fish in a suitable place to breed
Class；Aerobic zone --- anaerobic zone --- aerobic zone is sequentially formed in clarifier-tank；The Two Areas is anaerobic zone, clarifier-tank
Other waters surface are aerobic zone in region；
Hydrophyte natantia area coverage accounts for the 8%-12% of entire culture circulation system；
The culture circulation system provides water lift by the impeller being arranged at aquaculture pond and clarifier-tank handover marginal position
Circulation power；
The water body of drainage ditch flows into purification pool area；It is mentioned by water lift equipment to culture zone；
The impeller closes operation once every three days, closes 24 hours, increases the hydraulic detention time of purifying area, and impeller closes
When closing, culture zone starts spare emergency aeration oxygen replenishing.
2. improving the method for efficiency culturing pool treatment effeciency as described in claim 1, it is characterised in that: the cultivation circulation
The drainage system setting of system is divided into water circulation system and bottom blowdown system, the bottom blowdown system is every in cultivation pool area
It opens primary, each opening 15 minutes.
3. improving the method for efficiency culturing pool treatment effeciency as described in claim 1, it is characterised in that: the water purifying tank area
There are partition, the two sides for being located at the partition in first region and Two Areas mirror image among domain.
4. improving the method for efficiency culturing pool treatment effeciency as described in claim 1, it is characterised in that: the cultivation circulation
System is in rectangular configuration.
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| Application Number | Priority Date | Filing Date | Title |
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| CN201710007404.7A CN106698667B (en) | 2017-01-05 | 2017-01-05 | A method of improving efficiency culturing pool treatment effeciency |
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| CN201710007404.7A CN106698667B (en) | 2017-01-05 | 2017-01-05 | A method of improving efficiency culturing pool treatment effeciency |
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| CN106698667B true CN106698667B (en) | 2019-09-17 |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN107361008A (en) * | 2017-08-15 | 2017-11-21 | 遵义绥阳县芙蓉江鲟鱼繁养有限公司 | Modularization recirculated water sturgeon cultivation system |
| CN109095714B (en) * | 2018-08-29 | 2022-02-25 | 李磊 | Aerobic-anaerobic alternate sewage purification tank and purification process |
| CN110896911B (en) * | 2019-12-06 | 2022-03-29 | 天津农学院 | Method for constructing pond culture circulating water system |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| LV13066B (en) * | 2003-07-08 | 2003-12-20 | Sergejs Tracuks | Plant for fish breeding |
| CN201010606Y (en) * | 2007-05-11 | 2008-01-23 | 王宝贞 | Sewage treatment system with zero discharge of sludge |
| CN104170785A (en) * | 2014-08-22 | 2014-12-03 | 中国水产科学研究院渔业机械仪器研究所 | Flow control method of energy-efficiency breeding pool |
| CN104170786A (en) * | 2014-08-22 | 2014-12-03 | 中国水产科学研究院渔业机械仪器研究所 | Culture pond system capable of improving energy efficiency |
| CN105601033A (en) * | 2015-12-25 | 2016-05-25 | 浙江省淡水水产研究所 | In-situ aquaculture water repairing system |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20050183331A1 (en) * | 2003-07-02 | 2005-08-25 | Fountainhead L.L.C. | Super-enhanced aquatic floating island plant habitat |
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Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| LV13066B (en) * | 2003-07-08 | 2003-12-20 | Sergejs Tracuks | Plant for fish breeding |
| CN201010606Y (en) * | 2007-05-11 | 2008-01-23 | 王宝贞 | Sewage treatment system with zero discharge of sludge |
| CN104170785A (en) * | 2014-08-22 | 2014-12-03 | 中国水产科学研究院渔业机械仪器研究所 | Flow control method of energy-efficiency breeding pool |
| CN104170786A (en) * | 2014-08-22 | 2014-12-03 | 中国水产科学研究院渔业机械仪器研究所 | Culture pond system capable of improving energy efficiency |
| CN105601033A (en) * | 2015-12-25 | 2016-05-25 | 浙江省淡水水产研究所 | In-situ aquaculture water repairing system |
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