CN104542390A - Penaeus monodon industrialized high-density cultivating technology - Google Patents
Penaeus monodon industrialized high-density cultivating technology Download PDFInfo
- Publication number
- CN104542390A CN104542390A CN201410812435.6A CN201410812435A CN104542390A CN 104542390 A CN104542390 A CN 104542390A CN 201410812435 A CN201410812435 A CN 201410812435A CN 104542390 A CN104542390 A CN 104542390A
- Authority
- CN
- China
- Prior art keywords
- pond
- shrimp
- water
- penaeus monodon
- cultivating
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 241000238552 Penaeus monodon Species 0.000 title claims abstract description 25
- 238000005516 engineering process Methods 0.000 title abstract description 14
- 241000238557 Decapoda Species 0.000 claims abstract description 91
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 82
- 238000009360 aquaculture Methods 0.000 claims abstract description 51
- 244000144974 aquaculture Species 0.000 claims abstract description 51
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims abstract description 26
- 238000004062 sedimentation Methods 0.000 claims abstract description 26
- 102000004169 proteins and genes Human genes 0.000 claims abstract description 23
- 108090000623 proteins and genes Proteins 0.000 claims abstract description 23
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 15
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 15
- 229910052757 nitrogen Inorganic materials 0.000 claims abstract description 15
- 241000894006 Bacteria Species 0.000 claims abstract description 14
- 241000195493 Cryptophyta Species 0.000 claims abstract description 12
- 238000000034 method Methods 0.000 claims description 39
- 238000009395 breeding Methods 0.000 claims description 37
- 230000001488 breeding effect Effects 0.000 claims description 37
- 230000000384 rearing effect Effects 0.000 claims description 31
- 230000008569 process Effects 0.000 claims description 21
- 238000005189 flocculation Methods 0.000 claims description 19
- 230000016615 flocculation Effects 0.000 claims description 19
- 238000010923 batch production Methods 0.000 claims description 13
- 241000251468 Actinopterygii Species 0.000 claims description 12
- 238000001556 precipitation Methods 0.000 claims description 11
- 230000009286 beneficial effect Effects 0.000 claims description 8
- 238000010438 heat treatment Methods 0.000 claims description 8
- 238000012544 monitoring process Methods 0.000 claims description 8
- 241000193830 Bacillus <bacterium> Species 0.000 claims description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 6
- 229910052760 oxygen Inorganic materials 0.000 claims description 6
- 239000001301 oxygen Substances 0.000 claims description 6
- 239000002351 wastewater Substances 0.000 claims description 5
- 238000000746 purification Methods 0.000 claims description 4
- 238000003860 storage Methods 0.000 claims description 4
- 230000009471 action Effects 0.000 claims description 3
- 230000008901 benefit Effects 0.000 abstract description 7
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 abstract description 5
- 201000010099 disease Diseases 0.000 abstract description 5
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 abstract description 5
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 abstract description 4
- 238000003912 environmental pollution Methods 0.000 abstract description 4
- 239000003814 drug Substances 0.000 abstract description 3
- 238000006213 oxygenation reaction Methods 0.000 abstract description 3
- 230000004083 survival effect Effects 0.000 abstract description 3
- 229940079593 drug Drugs 0.000 abstract description 2
- 238000012258 culturing Methods 0.000 description 16
- 230000008859 change Effects 0.000 description 6
- 238000004519 manufacturing process Methods 0.000 description 5
- 244000005700 microbiome Species 0.000 description 5
- 230000007423 decrease Effects 0.000 description 4
- 230000009467 reduction Effects 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 230000001186 cumulative effect Effects 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 230000001717 pathogenic effect Effects 0.000 description 3
- 239000013535 sea water Substances 0.000 description 3
- 241001465754 Metazoa Species 0.000 description 2
- 230000001154 acute effect Effects 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000002207 metabolite Substances 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 230000001954 sterilising effect Effects 0.000 description 2
- 238000003786 synthesis reaction Methods 0.000 description 2
- 201000004569 Blindness Diseases 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- 241000238553 Litopenaeus vannamei Species 0.000 description 1
- 230000018199 S phase Effects 0.000 description 1
- 241000318927 Shrimp white spot syndrome virus Species 0.000 description 1
- 241000700605 Viruses Species 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000003242 anti bacterial agent Substances 0.000 description 1
- 229940088710 antibiotic agent Drugs 0.000 description 1
- 239000000427 antigen Substances 0.000 description 1
- 102000036639 antigens Human genes 0.000 description 1
- 108091007433 antigens Proteins 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 238000012937 correction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- 238000006073 displacement reaction Methods 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 239000002360 explosive Substances 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 235000012631 food intake Nutrition 0.000 description 1
- 235000021393 food security Nutrition 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 210000000987 immune system Anatomy 0.000 description 1
- 230000036039 immunity Effects 0.000 description 1
- 238000009364 mariculture Methods 0.000 description 1
- 235000013379 molasses Nutrition 0.000 description 1
- 150000002829 nitrogen Chemical class 0.000 description 1
- GQPLMRYTRLFLPF-UHFFFAOYSA-N nitrous oxide Inorganic materials [O-][N+]#N GQPLMRYTRLFLPF-UHFFFAOYSA-N 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 244000052769 pathogen Species 0.000 description 1
- 239000006041 probiotic Substances 0.000 description 1
- 235000018291 probiotics Nutrition 0.000 description 1
- 238000003908 quality control method Methods 0.000 description 1
- 238000010992 reflux Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 238000003809 water extraction Methods 0.000 description 1
Classifications
-
- 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
-
- 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
- A01K63/042—Introducing gases into the water, e.g. aerators, air pumps
-
- 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
- A01K63/045—Filters for aquaria
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/80—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
- Y02A40/81—Aquaculture, e.g. of fish
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Marine Sciences & Fisheries (AREA)
- Animal Husbandry (AREA)
- Biodiversity & Conservation Biology (AREA)
- Farming Of Fish And Shellfish (AREA)
Abstract
The invention provides a penaeus monodon industrialized high-density cultivating technology, comprising a young shrimp coarse standard pond, an intermediate cultivating pond, an adult shrimp cultivating pond, a rotary-drum microstrainer, an air-sifter type protein separator, a positive-negative biological processor, a purifying device, a sedimentation tank, an algae biological processor and a controller. According to the penaeus monodon industrialized high-density cultivating technology, the problems that the prawn survival rate is low, the benefit and yield are not prominent, the occupied area is overlarge, and the environmental pollution is severe are fundamentally solved through cultivating penaeus monodon by utilization of industrialized circulating water; by employment of grading multistage cultivation, the aquaculture water space can be sufficiently utilized, the water quality is guaranteed, the possibility of disease occurrence is reduced, the cultivating success rate is improved, drugs are prevented from being used, and the food safety is guaranteed; organic carbon is added in the aquaculture water through a biological floccules device so as to adjust the proportion of carbon to nitrogen, and sufficient oxygenation is combined at the same time, so that the growth of heterotrophic bacteria in the water can be promoted, ammonia nitrogen and nitrite nitrogen are reduced up to 98-100%, the feed quantity required for cultivating creatures is reduced, and the benefit is increased.
Description
Technical field
The invention belongs to aquaculture technical field, especially relate to a kind of Penaeus monodon batch production high-density breeding technique.
Background technology
China is engaged in one of aquaculture country with the longest history in the world.Southern “ Yu Ponds " and " port support " mode in the north continued centuries.Since the establishment of the nation, along with the attention of country to agricultural working and the effort of waterman author, the aquaculture industry of China is flourish, and within 2012, China Water product gross yield reaches 5,906 ten thousand tons, wherein cultured output 4,305 ten thousand tons, within continuous 24 years, ranks first in the world.
Prawn culturing is one of representational industry of most in culture fishery.After the serious puzzlement that experienced by nineteen nineties explosive disease, global prawn culturing enters the developing stage of a more rationality in recent years.One of Chinese major country of production as cultured prawn, the output of Chinese shrimps in culture is 2,420,000 tons, wherein cultured prawn output 1,530,000 tons, and mariculture prawn output is 870,000 tons, estimates to account for more than 30% of Global Sea Surface shrimp aquaculture output.
The prawn culturing of Efficiency in Buildings in Tianjin Area is the model area of northern cultivating penaeus monodon always, and aquaculture model mainly contains: pond high density culture, the large extensive extensive cultivation of the water surface, Fish-shrimp mix-culture, Mixed cultivation of prawn and crab, membranous system cultural technique etc.But in the process developed rapidly in Tianjin cultivating penaeus monodon industry, also occurred some distinct issues in recent years, pond culture production model reveals all disadvantages.
One, aquaculture management technology is also in empirical, and blindness is very serious.High density culture water body is by cultivation early stage and later stage, day and night, add water and change water, bait throwing in medication, weather conditions, the impact of micropopulation, change of water quality and prawn change are in acute variation, do not have quantizating index, can not accurate controlling and adjustment, often delayed to the correction of water body and breeding situations.
They are two years old, under high-density breeding pattern, the excreta of cultivated animals is deposited in water with the bait residue being rich in high protein, the method that in production, water is frequently changed in normal employing is diluted or reduces the concentration of harmful substance, especially the cultivation later stage has been arrived, wastewater displacement is extremely acute especially to be strengthened, contaminated environment, the serious sustainable health development hindering the sector.Research display, it is the one of the main reasons of the continuous decline causing China coastal seas seawater quality that a large amount of undressed breeding wastewaters is directly discharged into marine.In recent ten years, China coastal seas expands one times lower than the oceanic area of a class sea water quality standard, four classes and surpass the water surface area of four class sea water quality standards more than 50,000 square kilometres, fishery biologic environment constantly worsens, and prawn culturing production sustainable development is subject to severe challenge.
Its three, current high density culture pattern investment is large, but benefit and output are not given prominence to, the output of current 1000 ~ 1500 kgs/acre, if cultivation success rate is lower than 60%, the economic benefit produced is just very limited, be difficult to continue to maintain produce, more can not continue in environment, transformation.
In sum, cultivating penaeus monodon industry must be thought deeply again to the technology of all production links of this industry, changes traditional breeding way, sets up new aquaculture model with healthy aquaculture viewpoint, to strengthen the control ability to pathogenic virus and environment.Grope the new technology being suitable for Guangdong Province's prawn industry in time, original cultural technique is upgraded, develop new aquaculture model.Industrialization water circulation cultural technique is because realizing high-density breeding in indoor, and environmental pollution is little, the problems such as can avoid the discharge of breeding pollution thing, abuse of antibiotics, disease are difficult to control and escape the ecocatastrophe that causes.
The present invention is applying biological floc sedimentation technology in aquaculture, and it has reduction food consumption, reduces the features such as aquaculture wastewater discharge.The external existing example that this technology is applied in recent years, McIntosh and Avnimelech etc. introduce biological flocculation technology in water circulation system, find to make cultivated animals bring up to about 45% to the utilization ratio of protein by 25%; Burford etc. utilize isotope N to follow the trail of cultured prawn to the picked-up of biological flocculation and utilization, show that the nitrogen nearly 18% ~ 29% that cultured prawn absorbs every day naturally comes from biological flocculation; Panjaitan etc. further research also find, utilize the prawn culturing pond of biological flocculation technology, feed usage amount can reduce 30%.
Summary of the invention
The problem to be solved in the present invention is to provide a kind of Penaeus monodon batch production high-density breeding technique, this technique solves the difficult problem in traditional cultivating penaeus monodon industry, and fundamentally change prawn survival rate low, benefit and output are not given prominence to, the difficult problems such as floor space is excessive, and environmental pollution is serious.
For solving the problems of the technologies described above, the technical solution used in the present invention is:
A kind of Penaeus monodon batch production high-density breeding technique, it comprises shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, rotary drum Microfilter, air sifter formula protein separator, pros-and-cons type biological processor, purifier, sedimentation basin, algae bio treatment pond and controller, described shrimp seedling standard crude pool, described intermediate rearing pond, the bottom in described one-tenth shrimp aquaculture pond is connected respectively by pipeline, described shrimp seedling standard crude pool, described intermediate rearing pond, biological flocculation device is respectively arranged with, described shrimp seedling standard crude pool in described one-tenth shrimp aquaculture pond, described intermediate rearing pond, waste water in described one-tenth shrimp aquaculture pond flows to described rotary drum Microfilter respectively by lift pump, clear water after the process of described rotary drum Microfilter flows to air sifter formula protein separator, and then flow to pros-and-cons type biological processor, the water of described pros-and-cons type biological processor process enters described purifier, and the water through purifier purification turns back to described shrimp seedling standard crude pool, described intermediate rearing pond, described one-tenth shrimp aquaculture pond, the precipitation stayed through the process of described rotary drum Microfilter enters described sedimentation basin, precipitation through the process of described air sifter formula protein separator flows to described sedimentation basin, microdeposit through described pros-and-cons type biological processor flows to described sedimentation basin, algae bio treatment pond is flowed into, described shrimp seedling standard crude pool after the precipitation of described sedimentation basin adds clear water, described intermediate rearing pond, described one-tenth shrimp aquaculture pond, described rotary drum Microfilter, described air sifter formula protein separator, described pros-and-cons type biological processor, described sedimentation basin, described treatment pond pipeline is each other respectively arranged with control valve, and described controller is by control valve described in control circui.
Described shrimp seedling standard crude pool, described intermediate rearing pond, described one-tenth shrimp aquaculture pond are connected with storage oxygen device respectively.
Described shrimp seedling standard crude pool, described intermediate rearing pond, described one-tenth shrimp aquaculture pond are provided with automatic monitoring of water quality device, automatic bait-laying device for fish, self-heating apparatus, described automatic monitoring of water quality device will detect that signal sends to described controller, and described controller is respectively to described automatic bait-laying device for fish, the order of described self-heating apparatus sending action.
Described automatic bait-laying device for fish is connected with described controller by electromotor.
Described biological flocculation device adds organic carbon and beneficial bacterium in breeding water body, regulates carbon and nitrogen ratio in breeding water body to be greater than 10.
Described controller is PLC cyclelog.
Described beneficial bacterium is bacillus.
It is low that the present invention fundamentally changes prawn survival rate by industrial circulating water cultivating Penaeus monodon, the difficult problems such as benefit and output are not given prominence to, and floor space is excessive, and environmental pollution is serious; The cultivation of classification multistage can make the space of breeding water body be fully used, and has ensured water quality, decreases the possibility that disease occurs, improves cultivation success rate, avoid the use of medicine, ensured food security; In breeding water body, add organic carbon by biological flocculation device and regulate carbon and nitrogen ratio, combine sufficient oxygenation simultaneously, heterotrophic bacteria growth in water can be promoted, the protein of the inorganic nitrogen synthesis making heterotrophic bacteria utilize aquaculture organism to discharge self, transform the inorganic nitrogen in water body, reduction ammonia nitrogen and nitrite nitrogen are up to 98 ~ 100%, both the problem of breeding water body harmful substance accumulation had been solved, turn improve the utilization ratio of protein, decrease the requirement of aquaculture organism to feed, add income.
Accompanying drawing explanation
Fig. 1 is the flow chart that the embodiment of the present invention provides.
Embodiment
Biological flocculation is based on heterotrophic microorganism in breeding water body, through the floccule that biological flocculation is formed in conjunction with organic matter, inanimate matter, protozoa and algae etc. in water body.Because the deficiency of heterotrophic microorganism kind and quantity in breeding water body and the growth and breeding of heterotrophic microorganism need to consume a large amount of carbon sources, therefore need reasonably to add beneficial bacterium and carbon source in aquaculture process, when in breeding water body during C/N=10, the breeding of heterotrophic microorganism raised growth in water body can be made to form biological flocculation and consume aquatic feeds by nitrification and denitrification effect to be dissolved into N in water body, can obviously reduce NO in water body
2-N and NH
3-N content, the organic matter in water body also can be changed into own cells material by heterotrophic microorganism, effectively can reduce chemical oxygen demand in water body (COD).Stimulated the immune system of Penaeus monodon by metabolite or surface antigen after beneficial bacterium in biological flocculation enters Penaeus monodon enteron aisle; itself and harmful bacteria compete nutrition and attachment site simultaneously; protection prawn by the infringement of pathogen, and then strengthens the non-specific immunity of Penaeus monodon.After biological flocculation is formed, can be ingested by fishes and shrimps and utilize and transform oneself protein matter.
The invention provides a kind of Penaeus monodon batch production high-density breeding technique, it comprises shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, rotary drum Microfilter, air sifter formula protein separator, pros-and-cons type biological processor, sedimentation basin, algae bio treatment pond and controller, shrimp seedling standard crude pool, intermediate rearing pond, the bottom in shrimp aquaculture pond is become to be connected respectively by pipeline, shrimp seedling standard crude pool, intermediate rearing pond, become in shrimp aquaculture pond and be respectively arranged with biological flocculation device, rotary drum Microfilter is connected to shrimp seedling standard crude pool by lift pump, intermediate rearing pond, become shrimp aquaculture pond, clear water after the process of rotary drum Microfilter flows to air sifter formula protein separator, and then flow to pros-and-cons type biological processor, the water of pros-and-cons type biological processor process enters purifier, be provided with UV sterilizing unit in purifier, the water through purifier purification turns back to shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, the precipitation that the process of rotary drum Microfilter stays enters sedimentation basin, and air sifter formula protein separator is connected to sedimentation basin, and pros-and-cons type biological processor connects sedimentation basin, and sedimentation basin is connected to algae bio treatment pond, shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, rotary drum Microfilter, air sifter formula protein separator, pros-and-cons type biological processor, sedimentation basin, treatment pond pipeline is each other respectively arranged with control valve, and controller is by the opening and closing of control circui control valve.
Embodiment
As shown in Figure 1, a kind of Penaeus monodon batch production high-density breeding technique, it comprises shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, rotary drum Microfilter, air sifter formula protein separator, pros-and-cons type biological processor, sedimentation basin, algae bio treatment pond and PLC cyclelog, shrimp seedling standard crude pool, intermediate rearing pond, the bottom in shrimp aquaculture pond is become to be connected respectively by pipeline, shrimp seedling standard crude pool, intermediate rearing pond, become in shrimp aquaculture pond and be respectively arranged with biological flocculation device, rotary drum Microfilter is connected to shrimp seedling standard crude pool by lift pump, intermediate rearing pond, become shrimp aquaculture pond, clear water after the process of rotary drum Microfilter flows to air sifter formula protein separator, and then flow to pros-and-cons type biological processor, the water of pros-and-cons type biological processor process enters purifier, be provided with UV sterilizing unit in purifier, the water through purifier purification turns back to shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, the precipitation that the process of rotary drum Microfilter stays enters sedimentation basin, precipitation through the process of air sifter formula protein separator flows to sedimentation basin, microdeposit through the process of pros-and-cons type biological processor flows to sedimentation basin, algae bio treatment pond is entered after precipitation adds clear water in sedimentation basin, after the process of algae in algae bio treatment pond, this water body turns back to rotary drum Microfilter, shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, rotary drum Microfilter, air sifter formula protein separator, pros-and-cons type biological processor, sedimentation basin, the control valve that treatment pond pipeline is each other provided with is connected with PLC cyclelog by circuit, and PLC cyclelog is by the opening and closing of control circui control valve.
Shrimp seedling standard crude pool, intermediate rearing pond, one-tenth shrimp aquaculture pond are connected with storage oxygen device respectively, and storage oxygen device utilizes ejector to be dissolved in water by pure oxygen, and forms the current of certain orientation, greatly improves oxygen-transfer efficiency.
Shrimp seedling standard crude pool, intermediate rearing pond, shrimp aquaculture pond is become to be provided with automatic monitoring of water quality device, automatic bait-laying device for fish, self-heating apparatus, automatic monitoring of water quality device, automatic bait-laying device for fish, self-heating apparatus is connected with PLC cyclelog respectively, automatic monitoring of water quality device will detect that water quality signal sends to PLC cyclelog, PLC cyclelog can according to water quality condition to automatic bait-laying device for fish, self-heating apparatus, the order of control valve sending action, automatic bait-laying device for fish is connected with PLC cyclelog by electromotor, increase PLC cyclelog and make its automatic monitoring of water quality device, automatic bait-laying device for fish, the Automated condtrol of self-heating apparatus is further strengthened.
Biological flocculation device adds organic carbon and beneficial bacterium in breeding water body, and regulate carbon and nitrogen ratio in breeding water body to be greater than 10, optimally, in breeding water body, carbon and nitrogen ratio are 12.Wherein, beneficial bacterium can be bacillus.In aquaculture, applicable probio has tens of kinds, wherein the most typical probio of bacillus, and bacillus commonly uses probiotics as one, and it is extremely strong to environment-adapting ability, not easily makes a variation, and metabolite is nontoxic, and extracellular enzyme is numerous.Bacillus consumes aquatic feeds by nitrification and denitrification effect and is dissolved into N in water body, can obviously reduce NO in water body
2-N and NH
3-N content, also can change into own cells material, effectively can reduce chemical oxygen demand in water body (COD) by the organic matter in water body.
Often overlap cultivating system and comprise 3 culturing pools: shrimp seedling standard crude pool (accounting for 8% of cumulative volume ratio), intermediate rearing pond (accounting for 23% of cumulative volume ratio) with become shrimp aquaculture district (accounting for 69% of cumulative volume ratio), communicated by pipeline bottom each culturing pool, be convenient to the pond of falling of shrimp.Prawn culturing process is divided into children's phase, mid-term, one-tenth shrimp phase 3 independently to cultivate the stage by system.Each stage is that culturing pools different in systems in which completes.Shrimp seedling is placed in 1 little culturing pool at first, and area accounts for about 8% of the system gross area.Cultivate 20 ~ 25 days, the shrimp of the long 3 ~ 4cm of body is transferred to the 2nd culturing pool; 2nd culturing pool area accounts for 23% of the gross area, cultivates 20 ~ 25 days, and the long 7 ~ 8cm shrimp of body is finally transferred to maximum culturing pool; 3rd pool area accounts for 69% of the gross area, then through the cultivation of about 20 ~ 25 days, shrimp just can reach listing specification.
Carbon and nitrogen ratio is regulated by adding organic carbon (molasses) in breeding water body, combine sufficient oxygenation simultaneously, heterotrophic bacteria growth in water can be promoted, the protein of the inorganic nitrogen synthesis making heterotrophic bacteria utilize aquaculture organism to discharge self, transform the inorganic nitrogen in water body, reduction ammonia nitrogen and nitrite nitrogen are up to 98 ~ 100%.Because the inorganic nitrogen in water is effectively transformed, decrease quantity of exchanged water, maintain the water temperature needed for aquaculture organism, make it possible to cultivate Environment of Litopenaeus vannamei Low under minimum quantity of exchanged water condition.Biological flocculation technology has the advantages such as biological safety high (avoiding the highly pathogenic outbreak of disease such as WSSV), low exchanged water rate, high-density breeding, feed coefficient are low, aquaculture cost reduction.Owing to adopting biological flocculation technology in culturing pool, the ammonia nitrogen in water body and nitrite nitrogen salt level can control in level of security.But in its breeding process, once occur ammonia nitrogen and nitrous nitrogen salt too high, can air-lift device be passed through, by the water extraction in culturing pool in rotary drum Microfilter, after precipitation, reflux back the clear water of upper one-tenth culturing pool, makes treated water Quality Control built in usable range.
Above one embodiment of the present of invention have been described in detail, but described content being only preferred embodiment of the present invention, can not being considered to for limiting practical range of the present invention.All equalizations done according to the present patent application scope change and improve, and all should still belong within patent covering scope of the present invention.
Claims (7)
1. a Penaeus monodon batch production high-density breeding technique, is characterized in that: it comprises shrimp seedling standard crude pool, intermediate rearing pond, become shrimp aquaculture pond, rotary drum Microfilter, air sifter formula protein separator, pros-and-cons type biological processor, purifier, sedimentation basin, algae bio treatment pond and controller, described shrimp seedling standard crude pool, described intermediate rearing pond, the bottom in described one-tenth shrimp aquaculture pond is connected respectively by pipeline, described shrimp seedling standard crude pool, described intermediate rearing pond, biological flocculation device is respectively arranged with, described shrimp seedling standard crude pool in described one-tenth shrimp aquaculture pond, described intermediate rearing pond, waste water in described one-tenth shrimp aquaculture pond flows to described rotary drum Microfilter respectively by lift pump, clear water after the process of described rotary drum Microfilter flows to air sifter formula protein separator, and then flow to pros-and-cons type biological processor, the water of described pros-and-cons type biological processor process enters described purifier, and the water through purifier purification turns back to described shrimp seedling standard crude pool, described intermediate rearing pond, described one-tenth shrimp aquaculture pond, the precipitation stayed through the process of described rotary drum Microfilter enters described sedimentation basin, precipitation through the process of described air sifter formula protein separator flows to described sedimentation basin, microdeposit through described pros-and-cons type biological processor flows to described sedimentation basin, algae bio treatment pond is flowed into, described shrimp seedling standard crude pool after the precipitation of described sedimentation basin adds clear water, described intermediate rearing pond, described one-tenth shrimp aquaculture pond, described rotary drum Microfilter, described air sifter formula protein separator, described pros-and-cons type biological processor, described sedimentation basin, described treatment pond pipeline is each other respectively arranged with control valve, and described controller is by control valve described in control circui.
2. a kind of Penaeus monodon batch production high-density breeding technique according to claim 1, is characterized in that: described shrimp seedling standard crude pool, described intermediate rearing pond, described one-tenth shrimp aquaculture pond are connected with storage oxygen device respectively.
3. a kind of Penaeus monodon batch production high-density breeding technique according to claim 1, it is characterized in that: described shrimp seedling standard crude pool, described intermediate rearing pond, described one-tenth shrimp aquaculture pond are provided with automatic monitoring of water quality device, automatic bait-laying device for fish, self-heating apparatus, described automatic monitoring of water quality device will detect that signal sends to described controller, and described controller is respectively to described automatic bait-laying device for fish, the order of described self-heating apparatus sending action.
4. a kind of Penaeus monodon batch production high-density breeding technique according to claim 3, is characterized in that: described automatic bait-laying device for fish is connected with described controller by electromotor.
5. a kind of Penaeus monodon batch production high-density breeding technique according to claim 1, is characterized in that: described biological flocculation device adds organic carbon and beneficial bacterium in breeding water body, regulates carbon and nitrogen ratio in breeding water body to be greater than 10.
6. a kind of Penaeus monodon batch production high-density breeding technique according to claim 1, is characterized in that: described controller is PLC cyclelog.
7. a kind of Penaeus monodon batch production high-density breeding technique according to claim 5, is characterized in that: described beneficial bacterium is bacillus.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410812435.6A CN104542390B (en) | 2014-12-22 | 2014-12-22 | Penaeus monodon industrialized high-density cultivating technology |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201410812435.6A CN104542390B (en) | 2014-12-22 | 2014-12-22 | Penaeus monodon industrialized high-density cultivating technology |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN104542390A true CN104542390A (en) | 2015-04-29 |
| CN104542390B CN104542390B (en) | 2017-01-11 |
Family
ID=53060328
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201410812435.6A Expired - Fee Related CN104542390B (en) | 2014-12-22 | 2014-12-22 | Penaeus monodon industrialized high-density cultivating technology |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN104542390B (en) |
Cited By (18)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104920258A (en) * | 2015-06-23 | 2015-09-23 | 陈小昌 | Penaeus monodon breeding method |
| CN105052791A (en) * | 2015-08-07 | 2015-11-18 | 中国水产科学研究院南海水产研究所 | Ecological effect and mixed culture method of sipunculus nudus |
| CN105850860A (en) * | 2016-06-27 | 2016-08-17 | 东乡县民惠水产养殖专业合作社 | Greenhouse pond loach culture system |
| CN106172121A (en) * | 2016-07-11 | 2016-12-07 | 青岛农业大学 | The method that Litopenaeus vannamei batch production shrimp Seedling salinization mark is thick |
| CN106689002A (en) * | 2016-12-15 | 2017-05-24 | 雷州市海威水产养殖有限公司 | Green healthy controllable industrial prawn culture method |
| CN106698820A (en) * | 2016-12-15 | 2017-05-24 | 雷州市海威水产养殖有限公司 | Water circulating treatment method for indoor prawn culture tank |
| CN107047406A (en) * | 2017-03-16 | 2017-08-18 | 广西精工海洋科技有限公司 | A kind of sea-farming method of Penaeus monodon |
| CN107691315A (en) * | 2017-08-30 | 2018-02-16 | 安徽鸿运生态农业有限公司 | A kind of cultural method for improving Penaeus monodon yield |
| CN107691329A (en) * | 2016-08-05 | 2018-02-16 | 章晓俊 | Inland batch production is pollution-free sea product cultivating system |
| CN108477041A (en) * | 2018-04-02 | 2018-09-04 | 天津农学院 | A kind of method of industrial aquaculture Penaeus monodon |
| CN109730007A (en) * | 2019-02-26 | 2019-05-10 | 南通龙洋水产有限公司 | A kind of breeding method of intensive circulating water culture system ecologic food chain |
| CN110663596A (en) * | 2019-10-23 | 2020-01-10 | 中国科学院海洋研究所 | Vertical isolation stepping type three-dimensional breeding workshop for continuously producing prawns and breeding method |
| CN111345255A (en) * | 2020-04-15 | 2020-06-30 | 广东梅华水产食品有限公司 | Totally-enclosed factory circulating water high-efficiency prawn breeding system and method |
| CN111937802A (en) * | 2020-08-20 | 2020-11-17 | 巨大(江苏)农业科技有限公司 | Circulating water and biological flocculation combined industrial prawn culture system |
| CN113994907A (en) * | 2020-12-31 | 2022-02-01 | 渤海水产科技(滨州)有限公司 | Method for breeding large-size salt pan shrimps |
| CN113994906A (en) * | 2020-12-31 | 2022-02-01 | 汇泰渤海水产有限责任公司 | Method for cultivating salt pan shrimps by rotation and rotation |
| CN114271229A (en) * | 2020-12-31 | 2022-04-05 | 渤海水产(滨州)有限公司 | Rotation-releasing and rotation-catching salt pan shrimp culture pond |
| CN114600821A (en) * | 2022-03-23 | 2022-06-10 | 泰安九章信息科技有限公司 | Energy-saving high-density circulating water culture method and system |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN201709241U (en) * | 2010-06-08 | 2011-01-19 | 中国水产科学研究院珠江水产研究所 | Ecological pond culturing system |
| CN102067824A (en) * | 2010-11-25 | 2011-05-25 | 中国水产科学研究院渔业机械仪器研究所 | Closed circulating seawater prawn pond culture system |
| WO2013020797A1 (en) * | 2011-08-09 | 2013-02-14 | Weber Ultrasonics Gmbh | Method for using vinasse |
| KR20130140495A (en) * | 2012-06-14 | 2013-12-24 | 지춘수 | Environment-freindly fish farm and method of fish farming environment-freindly |
| CN203492593U (en) * | 2013-10-18 | 2014-03-26 | 海南省水产研究所 | South America white shrimp indoor factorization cultivation device |
-
2014
- 2014-12-22 CN CN201410812435.6A patent/CN104542390B/en not_active Expired - Fee Related
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN201709241U (en) * | 2010-06-08 | 2011-01-19 | 中国水产科学研究院珠江水产研究所 | Ecological pond culturing system |
| CN102067824A (en) * | 2010-11-25 | 2011-05-25 | 中国水产科学研究院渔业机械仪器研究所 | Closed circulating seawater prawn pond culture system |
| WO2013020797A1 (en) * | 2011-08-09 | 2013-02-14 | Weber Ultrasonics Gmbh | Method for using vinasse |
| KR20130140495A (en) * | 2012-06-14 | 2013-12-24 | 지춘수 | Environment-freindly fish farm and method of fish farming environment-freindly |
| CN203492593U (en) * | 2013-10-18 | 2014-03-26 | 海南省水产研究所 | South America white shrimp indoor factorization cultivation device |
Non-Patent Citations (2)
| Title |
|---|
| 张利民等: "《水域营养生态学》", 31 July 2012, 海洋出版社 * |
| 马绍赛等: "《海水工厂化循环水工程化技术与高效养殖》", 31 January 2014, 海洋出版社 * |
Cited By (22)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104920258A (en) * | 2015-06-23 | 2015-09-23 | 陈小昌 | Penaeus monodon breeding method |
| CN105052791A (en) * | 2015-08-07 | 2015-11-18 | 中国水产科学研究院南海水产研究所 | Ecological effect and mixed culture method of sipunculus nudus |
| CN105850860A (en) * | 2016-06-27 | 2016-08-17 | 东乡县民惠水产养殖专业合作社 | Greenhouse pond loach culture system |
| CN105850860B (en) * | 2016-06-27 | 2018-09-25 | 江西省鑫萱农业开发有限公司 | A kind of greenhouse loach breeding system |
| CN106172121A (en) * | 2016-07-11 | 2016-12-07 | 青岛农业大学 | The method that Litopenaeus vannamei batch production shrimp Seedling salinization mark is thick |
| CN106172121B (en) * | 2016-07-11 | 2019-03-05 | 青岛农业大学 | The thick method of litopenaeus vannamei batch production shrimp seedling salinization mark |
| CN107691329A (en) * | 2016-08-05 | 2018-02-16 | 章晓俊 | Inland batch production is pollution-free sea product cultivating system |
| CN106698820A (en) * | 2016-12-15 | 2017-05-24 | 雷州市海威水产养殖有限公司 | Water circulating treatment method for indoor prawn culture tank |
| CN106689002A (en) * | 2016-12-15 | 2017-05-24 | 雷州市海威水产养殖有限公司 | Green healthy controllable industrial prawn culture method |
| CN106689002B (en) * | 2016-12-15 | 2019-10-29 | 广东海威水产养殖有限公司 | A kind of batch production prawn healthy aquaculture method that green is controllable |
| CN107047406A (en) * | 2017-03-16 | 2017-08-18 | 广西精工海洋科技有限公司 | A kind of sea-farming method of Penaeus monodon |
| CN107691315A (en) * | 2017-08-30 | 2018-02-16 | 安徽鸿运生态农业有限公司 | A kind of cultural method for improving Penaeus monodon yield |
| CN108477041A (en) * | 2018-04-02 | 2018-09-04 | 天津农学院 | A kind of method of industrial aquaculture Penaeus monodon |
| CN109730007A (en) * | 2019-02-26 | 2019-05-10 | 南通龙洋水产有限公司 | A kind of breeding method of intensive circulating water culture system ecologic food chain |
| CN110663596A (en) * | 2019-10-23 | 2020-01-10 | 中国科学院海洋研究所 | Vertical isolation stepping type three-dimensional breeding workshop for continuously producing prawns and breeding method |
| CN111345255A (en) * | 2020-04-15 | 2020-06-30 | 广东梅华水产食品有限公司 | Totally-enclosed factory circulating water high-efficiency prawn breeding system and method |
| CN111937802A (en) * | 2020-08-20 | 2020-11-17 | 巨大(江苏)农业科技有限公司 | Circulating water and biological flocculation combined industrial prawn culture system |
| CN113994907A (en) * | 2020-12-31 | 2022-02-01 | 渤海水产科技(滨州)有限公司 | Method for breeding large-size salt pan shrimps |
| CN113994906A (en) * | 2020-12-31 | 2022-02-01 | 汇泰渤海水产有限责任公司 | Method for cultivating salt pan shrimps by rotation and rotation |
| CN114271229A (en) * | 2020-12-31 | 2022-04-05 | 渤海水产(滨州)有限公司 | Rotation-releasing and rotation-catching salt pan shrimp culture pond |
| CN114600821A (en) * | 2022-03-23 | 2022-06-10 | 泰安九章信息科技有限公司 | Energy-saving high-density circulating water culture method and system |
| CN114600821B (en) * | 2022-03-23 | 2023-12-26 | 泰安九章康促生物科技有限公司 | Energy-saving high-density circulating water culture method and system |
Also Published As
| Publication number | Publication date |
|---|---|
| CN104542390B (en) | 2017-01-11 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104542390B (en) | Penaeus monodon industrialized high-density cultivating technology | |
| CN101933489B (en) | Water circulation system and method for breeding marine fishes inland | |
| CN101120661B (en) | Ecological fishery cultivating device based on composite vertical current artificial wet land | |
| CN107047429A (en) | VHD industrializes pond ecological breeding system and its regulation and control method | |
| CN105746393A (en) | Circulating water runway type shrimp aquaculture system and circulating water runway type shrimp aquaculture method | |
| Pérez-Rostro et al. | Biofloc, a technical alternative for culturing Malaysian prawn Macrobrachium rosenbergii | |
| CN107279022A (en) | A kind of aquatic products circulating water culture system and method based on biological flocculation and biomembrane | |
| CN102976492B (en) | Water ecological purification system and method | |
| CN106508762A (en) | Method for indoor recirculating aquaculture of crayfish | |
| CN204426348U (en) | A kind of ecologic breeding mixing net cage | |
| CN109122531B (en) | Method for culturing hilsa herring | |
| CN108401970A (en) | Fish, shrimp, algae, abalone and sea cucumber circulating water ecological comprehensive culture system | |
| CN207054517U (en) | A kind of aquatic products circulating water culture system based on biological flocculation and technology of biological membrane | |
| CN106719193A (en) | A kind of method of utilization biological flocculation technical optimization Environment of Litopenaeus vannamei Low seed rearing | |
| CN204443674U (en) | A kind of circulation | |
| CN104396838A (en) | Shrimp aquaculture method using bacteria-algae for balance | |
| CN108046520A (en) | A kind of low stimulating organism flocculation aquaculture method of low cost | |
| CN103641229B (en) | Method for regulating and controlling of water quality of Litopenaeus Vannamei culture pond | |
| CN208273900U (en) | Fish, shrimp, algae, abalone and sea cucumber circulating water ecological comprehensive culture system | |
| CN205082481U (en) | Use pond culture system of biological wadding group technique | |
| CN105918165A (en) | Overwintering method for aquaculture through brackish omni-directional flowing water | |
| CN108793646A (en) | A kind of landscape type domestic sewage ecologically treating system | |
| CN105052797A (en) | Black snapper cultivating method | |
| CN104737952B (en) | A kind of shallow water runway recognition system and method based on bioflocculation reactor | |
| CN108522362A (en) | A kind of Penaeus Vannmei multi items pond polyculture method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| TR01 | Transfer of patent right |
Effective date of registration: 20171228 Address after: 300192, 238 Bai Causeway Road, Tianjin, Nankai District Patentee after: Tianjin Xinjin cotier Technology Development Co.,Ltd. Address before: 300000 Tianjin city Xiqing District temple town Qing Ning Hou Cunjin green farm west 500 meters Patentee before: TIANJIN MAOLIN AQUACULTURE CO.,LTD. |
|
| TR01 | Transfer of patent right | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20170111 Termination date: 20211222 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |