CN111919808A - Comprehensive fish and shrimp breeding purification system - Google Patents
Comprehensive fish and shrimp breeding purification system Download PDFInfo
- Publication number
- CN111919808A CN111919808A CN202010826074.6A CN202010826074A CN111919808A CN 111919808 A CN111919808 A CN 111919808A CN 202010826074 A CN202010826074 A CN 202010826074A CN 111919808 A CN111919808 A CN 111919808A
- Authority
- CN
- China
- Prior art keywords
- water
- pond
- purification
- tank
- channel
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 238000000746 purification Methods 0.000 title claims abstract description 128
- 241000238557 Decapoda Species 0.000 title claims abstract description 54
- 241000251468 Actinopterygii Species 0.000 title claims abstract description 25
- 238000009395 breeding Methods 0.000 title description 16
- 230000001488 breeding effect Effects 0.000 title description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 333
- 238000003860 storage Methods 0.000 claims abstract description 62
- 244000144974 aquaculture Species 0.000 claims abstract description 40
- 238000009360 aquaculture Methods 0.000 claims abstract description 39
- 239000002131 composite material Substances 0.000 claims abstract description 25
- 238000002955 isolation Methods 0.000 claims abstract description 9
- 239000002351 wastewater Substances 0.000 claims abstract description 7
- 241000196324 Embryophyta Species 0.000 claims description 68
- 241000252234 Hypophthalmichthys nobilis Species 0.000 claims description 30
- 238000009826 distribution Methods 0.000 claims description 29
- 238000004062 sedimentation Methods 0.000 claims description 22
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 16
- 239000001301 oxygen Substances 0.000 claims description 16
- 229910052760 oxygen Inorganic materials 0.000 claims description 16
- 238000007667 floating Methods 0.000 claims description 14
- 244000005700 microbiome Species 0.000 claims description 14
- 239000000945 filler Substances 0.000 claims description 12
- 241001465754 Metazoa Species 0.000 claims description 10
- 238000011144 upstream manufacturing Methods 0.000 claims description 9
- 239000004568 cement Substances 0.000 claims description 7
- 235000013311 vegetables Nutrition 0.000 claims description 6
- 240000000691 Houttuynia cordata Species 0.000 claims description 5
- 235000013719 Houttuynia cordata Nutrition 0.000 claims description 5
- 240000008436 Ipomoea aquatica Species 0.000 claims description 5
- 235000019004 Ipomoea aquatica Nutrition 0.000 claims description 4
- 241000411851 herbal medicine Species 0.000 claims description 4
- 238000001556 precipitation Methods 0.000 claims description 4
- 239000013505 freshwater Substances 0.000 claims description 3
- 238000012806 monitoring device Methods 0.000 claims description 2
- 239000000758 substrate Substances 0.000 claims 2
- 241000143060 Americamysis bahia Species 0.000 claims 1
- 241000252500 Ictalurus Species 0.000 claims 1
- 241000252498 Ictalurus punctatus Species 0.000 abstract description 15
- 238000012544 monitoring process Methods 0.000 abstract description 13
- 239000008213 purified water Substances 0.000 abstract description 3
- 241001659573 Centriscus scutatus Species 0.000 abstract 1
- 241000237858 Gastropoda Species 0.000 description 15
- 230000008901 benefit Effects 0.000 description 9
- 241000195493 Cryptophyta Species 0.000 description 7
- 238000012258 culturing Methods 0.000 description 7
- 238000000034 method Methods 0.000 description 7
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 6
- 238000005276 aerator Methods 0.000 description 6
- 238000010586 diagram Methods 0.000 description 6
- 238000009313 farming Methods 0.000 description 6
- 238000012856 packing Methods 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- 238000010276 construction Methods 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 244000000010 microbial pathogen Species 0.000 description 5
- 238000012545 processing Methods 0.000 description 5
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 4
- 238000006213 oxygenation reaction Methods 0.000 description 4
- 230000002265 prevention Effects 0.000 description 4
- 231100000331 toxic Toxicity 0.000 description 4
- 230000002588 toxic effect Effects 0.000 description 4
- 244000025254 Cannabis sativa Species 0.000 description 3
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 3
- 241000700605 Viruses Species 0.000 description 3
- 229910021529 ammonia Inorganic materials 0.000 description 3
- 230000001174 ascending effect Effects 0.000 description 3
- 238000004891 communication Methods 0.000 description 3
- 230000006870 function Effects 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 230000004083 survival effect Effects 0.000 description 3
- 241000195967 Anthoceros Species 0.000 description 2
- 235000017060 Arachis glabrata Nutrition 0.000 description 2
- 244000105624 Arachis hypogaea Species 0.000 description 2
- 235000010777 Arachis hypogaea Nutrition 0.000 description 2
- 235000018262 Arachis monticola Nutrition 0.000 description 2
- 241000193830 Bacillus <bacterium> Species 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 2
- ZKQDCIXGCQPQNV-UHFFFAOYSA-N Calcium hypochlorite Chemical compound [Ca+2].Cl[O-].Cl[O-] ZKQDCIXGCQPQNV-UHFFFAOYSA-N 0.000 description 2
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 2
- 240000003826 Eichhornia crassipes Species 0.000 description 2
- 235000003283 Pachira macrocarpa Nutrition 0.000 description 2
- 206010057249 Phagocytosis Diseases 0.000 description 2
- 235000014676 Phragmites communis Nutrition 0.000 description 2
- 240000001085 Trapa natans Species 0.000 description 2
- 235000014364 Trapa natans Nutrition 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 239000007844 bleaching agent Substances 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 229910052802 copper Inorganic materials 0.000 description 2
- 239000010949 copper Substances 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 239000003814 drug Substances 0.000 description 2
- 229940079593 drug Drugs 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 235000008216 herbs Nutrition 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 238000009309 intensive farming Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000010813 municipal solid waste Substances 0.000 description 2
- 235000016709 nutrition Nutrition 0.000 description 2
- 235000020232 peanut Nutrition 0.000 description 2
- 230000008782 phagocytosis Effects 0.000 description 2
- 230000000243 photosynthetic effect Effects 0.000 description 2
- 238000009344 polyculture Methods 0.000 description 2
- 238000002360 preparation method Methods 0.000 description 2
- 235000009165 saligot Nutrition 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 241000894007 species Species 0.000 description 2
- 238000004659 sterilization and disinfection Methods 0.000 description 2
- 230000031068 symbiosis, encompassing mutualism through parasitism Effects 0.000 description 2
- 235000017166 Bambusa arundinacea Nutrition 0.000 description 1
- 235000017491 Bambusa tulda Nutrition 0.000 description 1
- 241000269333 Caudata Species 0.000 description 1
- 241000238424 Crustacea Species 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 241000238631 Hexapoda Species 0.000 description 1
- 241000238559 Macrobrachium Species 0.000 description 1
- 241000058338 Macrobrachium nipponense Species 0.000 description 1
- IOVCWXUNBOPUCH-UHFFFAOYSA-N Nitrous acid Chemical compound ON=O IOVCWXUNBOPUCH-UHFFFAOYSA-N 0.000 description 1
- 241000209490 Nymphaea Species 0.000 description 1
- 235000016791 Nymphaea odorata subsp odorata Nutrition 0.000 description 1
- 241000241034 Palaemon pugio Species 0.000 description 1
- 244000273256 Phragmites communis Species 0.000 description 1
- 244000082204 Phyllostachys viridis Species 0.000 description 1
- 235000015334 Phyllostachys viridis Nutrition 0.000 description 1
- 241001263748 Pityopsis Species 0.000 description 1
- 241000700141 Rotifera Species 0.000 description 1
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 1
- 235000004519 Yucca filamentosa Nutrition 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 239000011425 bamboo Substances 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 238000004061 bleaching Methods 0.000 description 1
- 235000012255 calcium oxide Nutrition 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 241001233037 catfish Species 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000003750 conditioning effect Effects 0.000 description 1
- 238000013480 data collection Methods 0.000 description 1
- 230000034994 death Effects 0.000 description 1
- 231100000517 death Toxicity 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 230000006806 disease prevention Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000009310 extensive farming Methods 0.000 description 1
- 230000035558 fertility Effects 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000011133 lead Substances 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000002985 plastic film Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 239000011150 reinforced concrete Substances 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 230000028327 secretion Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000003643 water by type Substances 0.000 description 1
Images
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
- 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
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G9/00—Cultivation in receptacles, forcing-frames or greenhouses; Edging for beds, lawn or the like
- A01G9/02—Receptacles, e.g. flower-pots or boxes; Glasses for cultivating flowers
-
- 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
-
- 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
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Biodiversity & Conservation Biology (AREA)
- Marine Sciences & Fisheries (AREA)
- Animal Husbandry (AREA)
- Engineering & Computer Science (AREA)
- Biotechnology (AREA)
- Botany (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Farming Of Fish And Shellfish (AREA)
Abstract
本发明提供了一种综合养殖鱼虾的净化系统,其包括复合垂直潜流湿地用于对水源进行初步净化;河道通过水管与复合垂直潜流湿地相连接,进一步净化水质;净水池塘与河道的出口端通过溢流坝相隔,提升了水质;储水池塘的进口端与净水池塘的出口端通过潜流坝相隔,储水池塘的出口端通过隔离装置与复合垂直潜流湿地相隔,在对水质进行最终的净化和监测后,由水泵流入养殖池塘内;养殖池塘内混养青虾和斑点叉尾鮰,且养殖池塘内的养殖废水通过排水渠流入河道内进行净化,河道内的水质再流入净水池塘和储水池塘内实现循环净化;本发明采用四级净化水处理系统能够将养殖废水循环净化后使用,几乎达到零尾水排放,从而避免了对周围水体环境产生污染。
The invention provides a purification system for comprehensively cultivating fish and shrimp, which comprises a composite vertical underflow wetland for preliminary purification of water sources; a river channel is connected with the composite vertical underflow wetland through a water pipe to further purify water; the water purification pond and the outlet of the river channel The ends are separated by an overflow dam, which improves the water quality; the inlet end of the water storage pond and the outlet end of the water purification pond are separated by a submerged dam, and the outlet end of the water storage pond is separated from the composite vertical submerged wetland by an isolation device. After purification and monitoring, the water pump flows into the aquaculture pond; the green shrimp and channel catfish are mixed in the aquaculture pond, and the aquaculture wastewater in the aquaculture pond flows into the river channel through the drainage channel for purification, and the water quality in the river channel flows into the purified water pond and Circulation purification is realized in the water storage pond; the invention adopts a four-stage purified water treatment system, which can purify aquaculture wastewater before use, and achieve almost zero tail water discharge, thereby avoiding pollution to the surrounding water environment.
Description
技术领域technical field
本发明属于水产养殖技术领域,具体涉及一种综合养殖鱼虾的净化系统。The invention belongs to the technical field of aquaculture, and in particular relates to a purification system for comprehensively cultivating fish and shrimp.
背景技术Background technique
青虾学名日本沼虾(Macrobrachium nipponense),俗称河虾、草虾、湖虾,属甲壳纲(Crustacea)、沼虾属(Macrobrachium),广泛分布于我国淡水水域。其具有繁殖力高、适应性强、营养丰富、肉味鲜美和可常年上市等优点,是深受广大群众喜爱的名贵水产品,也是我国重要的淡水养殖虾类。目前市场上青虾由于天然产量的减少,人工养殖产量不高,始终满足不了市场需求。The green shrimp scientific name Macrobrachium nipponense, commonly known as river shrimp, grass shrimp, lake shrimp, belongs to Crustacea and Macrobrachium, and is widely distributed in freshwater waters in my country. It has the advantages of high fecundity, strong adaptability, rich nutrition, delicious meat and can be marketed all year round. At present, due to the reduction of natural production and the low output of artificial breeding, the green shrimp on the market has never been able to meet the market demand.
我国青虾养殖模式已经从原来的粗放型养殖模式逐渐过渡到集约化养殖模式。与传统养殖模式相比,集约化养殖具有单位水体产量高、养殖周期短和劳动效率高等优点。但是在这种集约化高密度的青虾养殖中,残饵和排泄物的数量超过了养殖池塘中微生物的自然分解能力,往往会打破水体微生态平衡,导致水质恶化,污染严重,甚至导致大规模死亡的现象频频发生。目前主要采用防控手段为加大渔药使用量和养殖池塘换水量,前者带来水产养殖动物品质的安全问题,已经引起人们的密切关注,而后者养殖尾水的排放已经给生态环境带来了不利影响。The shrimp farming model in my country has gradually transitioned from the original extensive farming model to the intensive farming model. Compared with the traditional farming mode, intensive farming has the advantages of high yield per unit of water, short farming cycle and high labor efficiency. However, in this intensive and high-density shrimp farming, the amount of residual bait and excrement exceeds the natural decomposition ability of microorganisms in the culture pond, which often breaks the micro-ecological balance of the water body, leading to deterioration of water quality, serious pollution, and even large Mass deaths occur frequently. At present, the main means of prevention and control are to increase the use of fishery drugs and the amount of water exchange in aquaculture ponds. The former brings about the safety of aquaculture animal quality, which has attracted people's close attention, while the discharge of the latter's aquaculture tailwater has brought a lot to the ecological environment. adverse effects.
斑点叉尾鮰(Ietalurus punetaus)属鲶形目、鮰科鱼类,原产于美洲,是全世界公认的适合淡水养殖的优良品种,具有食性杂、生长快、适应性广、抗病力强和肉质上乘等特点。斑点叉尾鮰在人工饲养条件下对投喂的配合饲料都能摄食,还摄食水中的天然饵料,比如水生昆虫、浮游动植物、轮虫、有机碎屑和藻类等。同时斑点叉尾鮰能吞噬小杂鱼和病虾,也能清理池塘中的残饵和藻类,鱼体表面可以分泌某些物质,能抑制虾蟹病毒。Channel catfish (Ietalurus punetaus) belongs to the order Catfish, and is native to the Americas. It is recognized as an excellent species for freshwater aquaculture in the world. Superior and other characteristics. Channel catfish can feed on formulated feeds in captivity, as well as natural food in the water, such as aquatic insects, phytoplankton, rotifers, organic detritus, and algae. At the same time, channel catfish can devour small trash fish and diseased shrimp, and can also clean up residual bait and algae in the pond. The surface of the fish can secrete certain substances, which can inhibit shrimp and crab viruses.
在水产养殖过程中,水体中不但会有残饵、排泄物和生物尸体等有毒有害的有机物质大量积累,而且还会积累大量的有毒有害无机物,如氨氮、硫化氢、亚硝酸等。鉴于上述原因,在青虾池塘养殖过程中就需要定期排放含有有毒有害物质的尾水,从而保证养殖对象的健康成长。目前多数情况下这些尾水是通过排水沟简单的排放,会造成较大的污染,也有养殖场会利用生物球或过滤器等对尾水进行过滤和处理,但是这种方式只能滤除尾水中的大颗粒杂质,达不到去除污染的目的;少数的养殖场会使用蛋白质分离器等设备来对尾水进行净化处理,然而,目前这些尾水通常是依次经过若干净化设备后就直接排放出去,经过处理的尾水中依然会存在较多的有毒有害物质,仍然会对环境造成较大的污染。In the process of aquaculture, not only a large amount of toxic and harmful organic substances such as residual bait, excrement and biological corpses will accumulate in the water body, but also a large amount of toxic and harmful inorganic substances, such as ammonia nitrogen, hydrogen sulfide, and nitrous acid, will accumulate. In view of the above reasons, it is necessary to regularly discharge tail water containing toxic and harmful substances in the process of shrimp pond culture, so as to ensure the healthy growth of the cultured objects. At present, in most cases, the tail water is simply discharged through the drainage ditch, which will cause greater pollution. There are also farms that use biological balls or filters to filter and treat the tail water, but this method can only filter out the tail water. The large particles of impurities in the water cannot achieve the purpose of removing pollution; a few farms will use equipment such as protein separators to purify the tail water. However, at present, the tail water is usually discharged directly after passing through several purification equipment in sequence. Going out, there will still be more toxic and harmful substances in the treated tail water, which will still cause greater pollution to the environment.
发明内容SUMMARY OF THE INVENTION
针对现有技术中的不足,本发明的目的是提供一种综合养殖鱼虾的净化系统。In view of the deficiencies in the prior art, the purpose of the present invention is to provide a purification system for comprehensively cultivating fish and shrimp.
为达到上述目的,本发明的解决方案是:In order to achieve the above object, the solution of the present invention is:
一种综合养殖鱼虾的净化系统,其包括复合垂直潜流湿地、河道、净水池塘、储水池塘和养殖池塘;A purification system for integrated fish and shrimp culture, comprising a composite vertical subsurface wetland, a river channel, a water purification pond, a water storage pond and a culture pond;
复合垂直潜流湿地,其用于对水源进行初步净化,改善水质,去除微生物;Composite vertical subsurface wetland, which is used for preliminary purification of water source, improvement of water quality, and removal of microorganisms;
河道,其通过水管与复合垂直潜流湿地相连接,经过河中水生动植物的净化和沉淀,进一步净化水质;The river channel, which is connected to the composite vertical subsurface wetland through water pipes, further purifies the water quality through the purification and precipitation of aquatic animals and plants in the river;
净水池塘,其与河道的出口端通过溢流坝相隔,经过其中的水生动植物、蔬菜和中草药的净化,提升了水质;The water purification pond, which is separated from the outlet end of the river by the overflow dam, improves the water quality through the purification of aquatic animals and plants, vegetables and Chinese herbal medicines;
储水池塘,其进口端与净水池塘的出口端通过潜流坝相隔,储水池塘的出口端通过隔离装置与复合垂直潜流湿地相隔,在对水质进行最终的净化和监测后,由水泵流入养殖池塘内;The inlet end of the water storage pond is separated from the outlet end of the water purification pond by a submerged flow dam, and the outlet end of the water storage pond is separated from the composite vertical submerged wetland by an isolation device. After the final purification and monitoring of the water quality, the water pump flows into the aquaculture. in the pond
养殖池塘,其通过进水渠与储水池塘、净水池塘、河道分别相隔,养殖池塘对称分布在排水渠两侧,养殖池塘内混养青虾和斑点叉尾鮰,且养殖池塘内的养殖废水通过排水渠流入河道内进行净化,河道内的水质再流入净水池塘和储水池塘内实现循环净化。The breeding pond is separated from the water storage pond, the water purification pond and the river channel by the intake channel. The breeding pond is symmetrically distributed on both sides of the drainage channel. The canal flows into the river channel for purification, and the water quality in the river channel flows into the water purification pond and the water storage pond to realize circular purification.
作为本发明的一种优选实施例,复合垂直潜流湿地从上至下包括由水管连接的调节池、初沉池、配水渠、下行潜流湿地、上行潜流湿地、生物预警池和清水池,调节池和初沉池并排布置,调节池和初沉池的下端设有若干配水渠,配水渠之间间隔设有下行潜流湿地和上行潜流湿地,配水渠的底部并排设有生物预警池和清水池,初沉池的顶部设有进水口,清水池的侧壁底端设有出水口,初沉池经过初步物理沉淀从而控制水流中的泥沙使其自然沉降,调节池对水体的pH值进行初步调节,之后通过配水渠相连的下行潜流湿地和上行潜流湿地,使得水质得到进一步净化,最后进入生物预警池和清水池对指示微生物进行监测并储存。As a preferred embodiment of the present invention, the composite vertical subsurface wetland includes, from top to bottom, an adjustment tank, a primary sedimentation tank, a distribution channel, a descending underflow wetland, an ascending underflow wetland, a biological early warning tank, and a clear water tank connected by water pipes. Arranged side by side with the primary sedimentation tank, there are several distribution channels at the lower ends of the adjustment tank and the primary sedimentation tank, and there are downward subsurface flow wetlands and upward subsurface flow wetlands between the distribution channels. The bottom of the distribution channel is equipped with a biological early warning pool and a clear water pool. The top of the primary sedimentation tank is provided with a water inlet, and the bottom end of the side wall of the clear water tank is provided with a water outlet. After adjustment, the water quality is further purified through the downstream subsurface wetland and the upstream subsurface wetland connected by the distribution channel, and finally enters the biological early warning tank and the clear water tank to monitor and store the indicator microorganisms.
作为本发明的一种优选实施例,下行潜流湿地从上至下包括水生植物、生态填料、防渗层和基底,设有下行潜流湿地的相邻配水渠间由集水管连接,水生植物和生态填料间设有布水管,集水管位于水生植物和生态填料的侧部,且位于防渗层的顶部。As a preferred embodiment of the present invention, the descending underflow wetland includes aquatic plants, ecological fillers, anti-seepage layers and bases from top to bottom, and adjacent water distribution channels with the descending underflow wetland are connected by a collecting pipe, and the aquatic plants and ecological A water distribution pipe is arranged between the packings, and the water collecting pipe is located on the side of the aquatic plants and the ecological packing, and is located on the top of the anti-seepage layer.
上行潜流湿地从上至下包括水生植物、生态填料、防渗层和基底,设有上行潜流湿地的相邻配水渠间由布水管连接,布水管位于生态填料的底部,防渗层的顶部。The ascending subsurface wetland includes aquatic plants, ecological packing, anti-seepage layer and base from top to bottom. The adjacent water distribution channels with the ascending subsurface wetland are connected by water distribution pipes. The water distribution pipes are located at the bottom of the ecological packing and the top of the anti-seepage layer.
作为本发明的一种优选实施例,河道包括河沟和护坡,护坡位于河沟的两侧,护坡内依次间隔设有“∩”型水泥护坡,河沟内水生植物的覆盖面积为水面的30-50%,“∩”型水泥护坡内种植湿生植物,河沟内投放鲢鳙鱼和螺蛳,河沟中水深为1.5-2m,pH值为7.2-8.5。As a preferred embodiment of the present invention, the river course includes a ditch and a slope protection, the slope protection is located on both sides of the river ditch, the slope protection is provided with "∩" type cement slope protection at intervals, and the coverage area of aquatic plants in the river ditch is 30-50% of the water surface , "∩" type cement slope protection planting wet plants, put silver carp and bighead carp and snail in the ditch, the water depth in the ditch is 1.5-2m, and the pH value is 7.2-8.5.
作为本发明的一种优选实施例,净水池塘包括生态浮床和增氧装置,增氧装置设置在净水池塘的底部,增加水体的含氧量使其维持在≥6mg/L,净水池塘内投放鲢鳙鱼和螺蛳,种植浮叶植物、挺水植物和沉水植物,生态浮床内种植空心菜和鱼腥草,净水池塘中水深为1.5-2m,pH值为7.2-8.5。As a preferred embodiment of the present invention, the water purification pond includes an ecological floating bed and an oxygenation device. The oxygenation device is arranged at the bottom of the water purification pond to increase the oxygen content of the water body to maintain it at ≥ 6 mg/L. Silver carp and bighead carp and snails were placed in it, floating-leaf plants, emerging plants and submerged plants were planted, and water spinach and Houttuynia cordata were planted in the ecological floating bed. The water depth in the water purification pond was 1.5-2m, and the pH value was 7.2-8.5.
作为本发明的一种优选实施例,储水池塘包括蓄水池和水质监测器,水质监测器设置在蓄水池的底部,蓄水池内种植浮叶植物、挺水植物和沉水植物,投放鲢鳙鱼和螺蛳,蓄水池中水深为2.5-2.8m,透明度为25-30cm,pH值为7.2-8.5。As a preferred embodiment of the present invention, the water storage pond includes a water storage pond and a water quality monitor, the water quality monitor is arranged at the bottom of the water storage pond, and floating leaf plants, emerging plants and submerged water plants are planted in the water storage pond. Silver carp and bighead carp and snails, the water depth in the reservoir is 2.5-2.8m, the transparency is 25-30cm, and the pH value is 7.2-8.5.
作为本发明的一种优选实施例,养殖池塘内设置实时监测装置,对水质的一些基本指标进行实时监测,如pH值、溶解氧和温度等。As a preferred embodiment of the present invention, a real-time monitoring device is installed in the culture pond to monitor some basic indicators of water quality in real time, such as pH value, dissolved oxygen and temperature.
由于采用上述方案,本发明的有益效果是:Owing to adopting the above-mentioned scheme, the beneficial effects of the present invention are:
第一、本发明采用包含复合垂直潜流湿地的四级净化水处理系统,同时配合实时监测设备,充分利用生态系统的剩余能量,能够将养殖用水循环净化后使用,对有机污染源进行全面合理处置,从而对养殖水进行充分利用,几乎达到零尾水排放,避免了对周围水体环境产生污染,节约水资源的同时利用高品质的水提升青虾的质量和存活率,不仅降低对生态的负担,而且实现生态与养殖效益共收,从而增加养殖用户的收入;另外,本发明的系统具有结构合理、绿色环保、能量转换率高和效益好等特点,是一个良性渔业生态环境,降低了生态风险,提高了生态效率,从而实现生产与生态协调统一。First, the present invention adopts a four-stage purified water treatment system including a composite vertical subsurface wetland, and at the same time cooperates with real-time monitoring equipment, makes full use of the remaining energy of the ecosystem, can purify the water for aquaculture before use, and comprehensively and rationally dispose of organic pollution sources. In this way, the aquaculture water is fully utilized to achieve almost zero tail water discharge, which avoids pollution to the surrounding water environment, saves water resources, and uses high-quality water to improve the quality and survival rate of green shrimp, which not only reduces the burden on the ecology, but also saves water resources. In addition, the system of the invention has the characteristics of reasonable structure, green environmental protection, high energy conversion rate and good benefit, etc., it is a benign fishery ecological environment, and reduces the ecological risk , improve the ecological efficiency, so as to achieve the coordination and unity of production and ecology.
第二、本发明将青虾和斑点叉尾鮰进行生态混养,斑点叉尾鮰能吞噬小杂鱼和病虾,也能清理池塘中的残饵和藻类,鱼体表面可以分泌某些物质,能抑制虾蟹病毒,从而使鱼虾和谐有机共存,互利共生,提高饵料利用率,降低养殖品种的发病几率,对水中的有机物利用更加充分,提高单位面积产量,增加效益,减少环境污染。Second, the present invention carries out ecological polyculture of green shrimp and channel catfish. Channel catfish can devour small trash fish and diseased shrimp, and can also clean up residual bait and algae in the pond. The surface of the fish can secrete certain substances, which can inhibit shrimp. Crab virus, so that fish and shrimp coexist harmoniously and organically, mutually beneficial symbiosis, improve the utilization rate of bait, reduce the incidence of aquaculture species, more fully utilize the organic matter in the water, increase the yield per unit area, increase efficiency, and reduce environmental pollution.
综上,本发明首先利用多级水净化循环系统将养殖用水循环使用,几乎达到零排放,避免了养殖废水对环境的影响。其次多级净化配备增设的在线监测设备,实时监测水中的溶氧、CO2、pH等多项指标,保证了养殖用水的水质,给虾和鱼提供一个适宜的环境,最后斑点叉尾鮰与青虾的混养又利用了斑点叉尾鮰清理残饵病虾,以及其分泌物可以抑制部分虾蟹病毒的多重优势配合下,既提高了青虾的存活率,又进一步提高了青虾的质量和产量。本发明一方面节约用水且减少了用药降低成本,另一方面提高了青虾的产量和质量且获得巨大的生态效益,增加收入,一增一减之间将养殖的经济效益最大化,从而提高养殖用户的收入。To sum up, the present invention firstly utilizes the multi-stage water purification and circulation system to recycle the water for aquaculture, which almost achieves zero discharge and avoids the impact of the aquaculture wastewater on the environment. Secondly, the multi-stage purification is equipped with additional online monitoring equipment to monitor the dissolved oxygen, CO 2 , pH and other indicators in the water in real time, which ensures the water quality of aquaculture water and provides a suitable environment for shrimp and fish. Finally, channel catfish and green shrimp The polyculture also takes advantage of channel catfish to clean up the residual bait and diseased shrimp, and its secretions can inhibit some shrimp and crab viruses. With the combination of multiple advantages, it not only improves the survival rate of green shrimp, but also further improves the quality and output of green shrimp. On the one hand, the present invention saves water and reduces the cost of drug use; on the other hand, it improves the output and quality of green shrimp and obtains huge ecological benefits and increases income. Income from farming users.
附图说明Description of drawings
图1为本发明的综合养殖鱼虾的净化系统模式图。FIG. 1 is a schematic diagram of a purification system for comprehensively farming fish and shrimp according to the present invention.
图2为本发明的一级净化沉降系统结构示意图。Figure 2 is a schematic structural diagram of the primary purification sedimentation system of the present invention.
图3为本发明的二级净化系统结构示意图。FIG. 3 is a schematic structural diagram of the secondary purification system of the present invention.
图4为本发明的三级净化系统结构示意图。FIG. 4 is a schematic structural diagram of the three-stage purification system of the present invention.
图5为本发明的四级净化储水系统结构示意图。FIG. 5 is a schematic structural diagram of the four-stage purification water storage system of the present invention.
图6为本发明中实施例的物联网系统运行模式图。FIG. 6 is an operation mode diagram of the Internet of Things system according to an embodiment of the present invention.
附图标记:1-水泵,2-配水渠,3-隔离装置,4-下行潜流湿地,5-上行潜流湿地,6-生物预警池,7-清水池,8-河道,9-溢流坝,10-生态浮床,11-净水池塘,12-潜流坝,13-蓄水池,14-调节池,15-初沉池,16-养殖池塘,17-排水渠,18-水质监测器,19-水管,20-水源,21-进水口,22-生态填料,23-集水管,24-基底,25-防渗层,26-出水口,27-布水管,28-进水渠,29-“∩”型水泥护坡,30-河沟,31-增氧装置,32-复合垂直潜流湿地,33-储水池塘。Reference numerals: 1-water pump, 2-distribution channel, 3-isolation device, 4-downward underflow wetland, 5-upward underflow wetland, 6-biological early warning pool, 7-clear water pool, 8-river channel, 9-overflow dam , 10-ecological floating bed, 11-purifying pond, 12-underflow dam, 13-reservoir, 14-regulation pond, 15-primary sedimentation pond, 16-culture pond, 17-drainage channel, 18-water quality monitor, 19-water pipe, 20-water source, 21-water inlet, 22-ecological packing, 23-water collection pipe, 24-base, 25-impermeable layer, 26-water outlet, 27-distribution pipe, 28-water inlet, 29- "∩" type cement slope protection, 30-he ditch, 31-aeration device, 32-composite vertical underflow wetland, 33-water storage pond.
具体实施方式Detailed ways
本发明提供了一种综合养殖鱼虾的净化系统。The invention provides a purification system for comprehensively cultivating fish and shrimp.
如图1所示,本发明的水源20首先经复合垂直潜流湿地32(一级净化沉降系统)初步净化,其次,通过水管进入河道8(二级净化系统)中被植物、浮游生物、微生物、底栖生物等净化,然后经溢流坝9流入净水池塘11(三级净化系统)中,污染物进一步被水生动物、植物吸收利用,水体再经潜流坝12过滤进入储水池塘33(四级净化储水系统)中,储水池塘33同时起到净化水质和蓄水监测的作用。经四级净化处理过的水作为养殖用水经进水泵1流入进水渠28,从而流入到养殖池塘16内,养殖池塘16中的养殖废水通过排水渠17直接注入二级净化系统河道8内,再依次流经三级净化系统和四级净化储水系统,最后再回到养殖池塘16进而形成一个“零”排放的循环养殖模式。采用四级联动净化水质,减少污染,从而达到生态效益和经济效益的双收。As shown in FIG. 1 , the water source 20 of the present invention is initially purified by the composite vertical subsurface wetland 32 (first-level purification sedimentation system), and secondly, it enters the river channel 8 (second-level purification system) through a water pipe and is surrounded by plants, plankton, microorganisms, Benthic organisms are purified, and then flow into the water purification pond 11 (three-level purification system) through the
具体地,本发明的综合养殖鱼虾的净化系统包括:复合垂直潜流湿地32、河道8、净水池塘11、储水池塘33和养殖池塘16;其中,复合垂直潜流湿地32用于对水源20进行初步净化,改善水质,去除微生物;河道8通过水管与复合垂直潜流湿地32连通,经过河中水生动植物的净化和沉淀,进一步净化水质;净水池塘11与河道8的出口端通过溢流坝9相隔,经过其中的水生动植物、蔬菜和中草药的净化,提高了水质净化;储水池塘33的进口端与净水池塘11的出口端通过潜流坝12相隔,储水池塘33的出口端通过隔离装置3与复合垂直潜流湿地32相隔,在对水质进行最终的净化和监测后,由水泵1流入养殖池塘16内;养殖池塘16通过进水渠28与储水池塘33、净水池塘11、河道8分别相隔,养殖池塘16对称分布在排水渠17两侧,养殖池塘16内混养青虾和斑点叉尾鮰,且养殖池塘16内的养殖废水通过排水渠17流入河道8内进行净化,河道8内的水质再流入净水池塘11和储水池塘33内实现循环净化。Specifically, the purification system for comprehensive fish and shrimp culture of the present invention includes: a composite
隔离装置3主要采用硬质驳岸的钢筋混凝土矮坝,设置在复合垂直潜流湿地32和储水池塘33之间、复合垂直潜流湿地32和养殖池塘16之间,从而起到隔离作用,养殖池塘16和河道8之间则有河道8两边的带护坡的河岸隔开。The
(1)、一级净化沉降系统的构建(1) Construction of a primary purification sedimentation system
如图1和图2所示,一级净化沉降系统中水源20会先流经第一部分调节池14与初沉池15,再流入第二部分下行潜流湿地4,下行潜流湿地4由水生植物、布水管27、生态填料22、集水管23、防渗层25和基底24组成,然后进入第三部分上行潜流湿地5,上行潜流湿地5由水生植物、布水管27、生态填料22、防渗层25和基底24组成,最后进入第四部分生物预警池6和清水池7,四个部分之间都由配水渠2和水管19进行连接。其中,作为第一级生物的复合垂直潜流湿地32,不仅可以初步改善水质,同时对指示微生物及病原微生物去除效果较好,降低虾和鱼的发病率,而且也有着蓄水节水的功效,从而降低成本。As shown in Figures 1 and 2, the water source 20 in the primary purification and sedimentation system will first flow through the first part of the
具体地,水源20先经过初沉池15和调节池14,初沉池15的顶部设有进水口21,初沉池15会对泥沙等经过初步物理沉淀即通过管道的开与关控制水流使其自然沉降,而调节池14会对水体的pH值等进行初步调节。之后通过配水渠2进入下行潜流湿地4,下行潜流湿地4自上而下包括水生植物、生态填料22、防渗层25和基底24,设有下行潜流湿地4的相邻配水渠2间由集水管23连接,水生植物和生态填料22间设有布水管27,集水管23位于水生植物和生态填料22的侧部,且位于防渗层25的顶部。水流经过时,水中的非离子氨、亚硝酸盐、病原微生物、藻类、铜、铅被水生植物吸收和被生态填料22吸附进而得到净化,且防渗层25阻止污水向地下水体渗透。再进入上行潜流湿地5,上行潜流湿地5从上而下包括水生植物、生态填料22、防渗层25和基底24,设有上行潜流湿地5的相邻配水渠2间由布水管27连接,布水管27位于生态填料22的底部,防渗层25的顶部。为了使得水质得到进一步净化,上行潜流湿地5和下行潜流湿地4种养凤眼莲、水花生、芦苇、蒲草、再力花等水生植物,并引入鲢鳙鱼和螺蛳,具体比例可以参考二级净化系统,也可因地制宜进行调节,最后进入生物预警池6和清水池7方便对指示微生物等指标进行监测并储存,具体地,生物预警池6对水中的指示微生物进行监控,以便人工随机采样监测;清水池7存储经过湿地净化过的水源水,以便逐级控水维持水流量,并经出水口26流入二级净化系统河道8内。综上,一级净化沉降系统对引进的水质进行初步净化,从而改善水质,同时对指示微生物及病原微生物去除效果较好,进一步降低虾和鱼的发病率。也有着蓄水节水的功效,从而降低成本。经测算,本级净化沉降系统的非离子氨、亚硝酸盐的平均去除率分别为35.47±6.84%、38.29±6.21%,对病原微生物中的总大肠菌群、藻类、铜、铅的去除率分别为68.1±6.8%、68.99±5.84%、33.70±10.14%、71.20±12.22%,透明度约达到10-15cm,pH值维持在7.2-8.5之间。Specifically, the water source 20 first passes through the
(2)、二级净化系统的构建(2) Construction of secondary purification system
如图1和图3所示,二级净化系统主要为河道8,水深1.5-2m,pH值维持在7.2-8.5之间,透明度约达到15-20cm,河道8包括河沟30和护坡,护坡位于河沟30的两侧进而稳固沙土,护坡内依次间隔设有“∩”型水泥护坡29,“∩”型水泥护坡29内种植湿生植物,河沟30内投放鲢鳙鱼和螺蛳,在河沟30的两侧种养凤眼莲、水花生等水生植物,用毛竹围栏固定,覆盖面积为水面的30-50%;在河沟30中放养规格为100-200g/尾的白鲢50-100尾/亩、鳙鱼30-50尾/亩;在河道底部放养150-300kg/亩螺蛳,通过植物、浮游生物、微生物、底栖生物等进一步净化,降低水中约15-20%的氨氮,进一步拦截固体残渣,并通过鲢鳙鱼和螺蛳进一步吞噬指示微生物及病原微生物。河道8在对水质进一步净化的基础上,起到将复合垂直潜流湿地32和净水池塘11相连接的作用。As shown in Figure 1 and Figure 3, the secondary purification system is mainly a
(3)、三级净化系统的构建(3) Construction of three-stage purification system
如图1和图4所示,三级净化系统为净水池塘11,溢流坝9位于净水池塘11左侧用于与二级净化系统隔离,水深约为1.5-2m,pH值维持在7.2-8.5之间,透明度约达到22-30cm。净水池塘11包括生态浮床10和增氧装置31,生态浮床10漂浮在净水池塘11的中央,净水池塘11的底部设有增氧装置31,增加水体的含氧量使其维持在≥6mg/L,净水池塘11内投放鲢鳙鱼和螺蛳,种植浮叶植物、挺水植物和沉水植物,生态浮床10内种植空心菜和鱼腥草。在净水池塘11内种植芦苇、蒲草、再力花等挺水植物,覆盖面积为水面的30%左右,种植如菹草、金鱼藻、轮叶黑藻、黄丝草等沉水植物,覆盖面积为20%左右,种植睡莲、菱角等浮叶植物,覆盖面积为10%左右,另外,可采用生态浮床10等设施种植蔬菜类如植空心菜和中草药类如鱼腥草等经济植物,覆盖面积为5%左右;在净水池塘11中放养鲢、鳙、螺蛳同二级净化系统,并根据净水池塘11面积配备增氧机或在底部安装微孔的增氧装置31,通过动植物吸收利用,使得水质进一步净化。降低水中约20-30%的氨氮,更进一步拦截固体残渣,并通过鲢鳙鱼和螺蛳的吞噬指将示微生物及病原微生物的含量再次降低,同时安装微孔的增氧装置31将水中的含氧量提升5-15%。综上,净水池塘11主要利用生态浮床10中养殖的蔬菜和中草药、水中栽种的植物和养殖的水生动物对水质作进一步净化提升,同时利用生态浮床10中所栽种的经济作物提升收益。As shown in Figures 1 and 4, the tertiary purification system is a water purification pond 11, the
(4)、四级净化储水系统的构建(4) Construction of a four-stage purification water storage system
如图1和图5所示,四级净化储水系统主要为储水池塘33,主要起到蓄水作用,水深约2.5-2.8m,透明度约25-30cm,pH值维持在7.2-8.5之间。储水池塘33包括蓄水池13和水质监测器18,水质监测器18设置在蓄水池13的左侧底部,潜流坝12位于蓄水池13左侧用于与净水池塘11隔离,水泵1置于蓄水池13靠近养殖池塘16侧用于向养殖池塘16供水,蓄水池13内种植浮叶植物、挺水植物和沉水植物,并放养鲢鳙鱼和螺蛳。在蓄水池13中种植浮叶植物、挺水植物和沉水植物同三级净化系统,覆盖面积分别为10%、20%和30%左右;在蓄水池13中放养白鲢、鳙鱼、螺蛳同三级净化系统。四级净化并进行储存,同时设有实时监测设备,从而实时监测水质,确保经四级净化储水系统出来的水质要符合NY/T5361-2016和SC/T9101-2007的规定,最后净化后的水进入养殖池塘16中。储水池塘33和养殖池塘16之间隔有进水渠28,储水池塘33中的水源经过水泵1流入养殖池塘16内,储水池塘33除了对上一级流入的水做最终净化之外,还起到蓄水和监测的作用,确保有足够的合格的水供养殖池塘16使用。As shown in Figure 1 and Figure 5, the four-stage purification water storage system is mainly a
(5)、养殖池塘的构建(5) Construction of aquaculture ponds
养殖池塘16在四级净化储水系统之后需要以下准备。The
如图1所示,养殖池塘16紧邻二级净化系统河道8,养殖池塘16和储水池塘33、净水池塘11之间间隔进水渠28。在本发明的具体实施例中,养殖池塘16分为6块养殖区域,养殖区域中紧邻河道8的一侧设置水质监测器18以监测水质,每三个养殖区域串联为一组,组与组之间设有排水渠17,养殖池塘16内的养殖废水通过排水渠17进入二级净化系统河道8内。其中,养殖池塘16为主要养殖区域,混养青虾和斑点叉尾鮰。As shown in FIG. 1 , the
<1>池塘准备:选取水源充足、进排水方便、面积为2.6亩的长方形池塘,东西走向,长宽比为5:3。三面环沟深1.5-2m,养殖池塘16水深与环沟持平,滩面坡比为1:2;进水口罩上过滤网(网目选择70目),且进水口与排水口呈对角设置;配置1.5kw微孔增氧机一台;在池塘四周设置双层塑料布,用木棍固定,并向池塘内倾斜15°,在养殖池塘16与二级净水系统相通的排水渠两侧放置实时监测设备,该监测设备包括摄像头、温度传感器、pH传感器、溶解氧传感器、CO2传感器和氨氮传感器,从而对养殖水的各项常规指标进行实时监测。<1> Pond preparation: Choose a rectangular pond with an area of 2.6 mu with sufficient water source, convenient inflow and drainage, east-west orientation, and an aspect ratio of 5:3. The depth of the ditch on three sides is 1.5-2m, the water depth of the
<2>清塘消毒:苗种放养前一个月将池塘暴晒一周,然后向池塘里加水至20cm,用漂白粉化水全池泼洒消毒,漂白粉用量为130-150kg/亩,7d后排干水。<2> Disinfection of ponds: Expose the pond to the sun for a week one month before the seedlings are stocked, then add water to the pond to 20cm, and spray the whole pond with bleaching powder for disinfection. The amount of bleaching powder is 130-150kg/mu, and the water is drained after 7 days.
<3>种草投螺:池塘消毒后种植水草,采用分畦间种,伊乐藻、金鱼藻、苦草和轮叶黑藻多品种套种,每畦栽种水草三行,行距为1.2m,畦与畦之间间隔2.4m,栽草行向与塘向垂直;清明节前向池塘内投放鲜活螺蛳,一次性投放400-500kg/亩。<3> Planting grass and throwing snails: After the pond is sterilized, plant aquatic plants, and use inter-planting in different borders. Multi-species interplanting of elegans, hornwort, bitter grass and black algae, three rows of aquatic plants are planted in each border, and the row spacing is 1.2m. The spacing between the borders is 2.4m, and the direction of planting grass is perpendicular to the direction of the pond; before the Qingming Festival, fresh and live snails are put into the pond at a time of 400-500kg/mu.
<4>苗种放养:青虾第一茬放养在2月上旬,放养规格为2.5-3cm/尾的种虾6-8kg/亩,第二茬放养在7月上旬,放养规格为0.5-0.8cm的虾苗3-5万尾/亩;斑点叉尾鮰苗种在3月中旬放养,规格为50-80g/尾,放养密度为1200-1500尾/亩,所放养虾种附肢齐全、体质健壮,所有苗种放养前均用3%食盐水溶液浸浴6min。<4> Seed stocking: The first crop of green shrimp is stocked in early February, and the stocking size is 6-8kg/mu of 2.5-3cm/tail, and the second crop is stocked in early July, with a stocking specification of 0.5-0.8 cm of shrimp fry is 30,000-50,000/mu; channel catfish fry are stocked in mid-March, with a size of 50-80g/tail, and a stocking density of 1200-1500/mu. The stocked shrimp species have complete appendages and a robust physique. , All seedlings were soaked in 3% saline solution for 6min before stocking.
<5>饲料投喂:青虾幼苗发育采用微量元素营养强化方法,成虾可投喂北京大北农科技集团股份有限公司的青虾配合饲料,投饲量根据季节、天气、水质和摄食情况灵活调整。<5> Feeding: The development of green shrimp seedlings adopts the method of nutritional fortification with trace elements. The adult shrimp can be fed with the green shrimp compound feed of Beijing Dabeinong Technology Group Co., Ltd. The feeding amount depends on the season, weather, water quality and feeding situation. Flexible adjustment.
<6>水质管理:保持池塘水pH值维持在7.2-8.5之间、透明度为20-25cm、溶解氧为5.5-6.5mg/L以上;夏季高温天气保持最高水位,每隔10d换一次水,每次换水量的水位为20cm;6-9月期间每15d使用芽孢杆菌和光合细菌一次,每月用生石灰改良水质;高温季节晴天中午开增氧机3h,阴天时次日清晨开增氧机2h,连绵阴雨天时半夜开增氧机5h。<6> Water quality management: keep the pH value of the pond water between 7.2-8.5, the transparency of 20-25cm, and the dissolved oxygen above 5.5-6.5mg/L; maintain the highest water level in high temperature weather in summer, and change the water every 10d. The water level of each water change is 20cm; Bacillus and photosynthetic bacteria are used every 15 days from June to September, and quicklime is used to improve the water quality every month; the aerator is turned on for 3 hours at noon on sunny days in high temperature season, and the aerator is turned on the next morning in cloudy days 2h, and the aerator is turned on for 5h in the middle of the night on continuous cloudy and rainy days.
<7>病害防治:坚持以防为主、防重于治和防治结合的原则,苗种放养前用3%食盐水浸浴10min;6-9月份,每隔15d使用一次芽孢杆菌和光合细菌;生长季节每月用8-10kg/亩的漂白粉化水全池泼洒。<7> Disease prevention and control: Adhere to the principle of prevention first, prevention is more important than cure and prevention and control, soak the seedlings with 3% salt water for 10min before stocking; from June to September, use Bacillus and photosynthetic bacteria every 15d ; Sprinkle the whole pond with 8-10kg/mu bleaching and pulverizing water every month during the growing season.
<8>捕捞上市:第一茬放养青虾在当年6月份陆续起捕上市,第二茬在第二年1月份起捕上市;斑点叉尾鮰和鲢鳙在第二年1月份干塘起捕上市。<8> Fishing and listing: The first batch of free-ranging green shrimp will be caught and listed in June of that year, and the second batch will be caught and listed in January of the second year; channel catfish and silver carp will be caught and listed in dry ponds in January of the second year. .
以下结合实施例对本发明作进一步的说明。The present invention will be further described below in conjunction with the examples.
实施例:Example:
采用上述养殖模式在江苏省盐城市科技试验示范基地进行养殖实验,具体养殖方法包括:Breeding experiments were carried out at the Science and Technology Experimental Demonstration Base in Yancheng City, Jiangsu Province using the above-mentioned breeding mode. The specific breeding methods include:
(1)将水源地水引入复合垂直潜流湿地对其进行初步净化,对水体中的非离子氨、亚硝酸盐、总大肠菌群、藻类、铜、铅、泥沙进行去除和沉淀,使得水体的透明度约达到15cm,pH值维持在7.8,含氧量达到4mg/L;(1) The source water is introduced into the composite vertical subsurface wetland for preliminary purification, and the non-ionic ammonia, nitrite, total coliforms, algae, copper, lead, and sediment in the water body are removed and precipitated, so that the water body is The transparency reaches about 15cm, the pH value is maintained at 7.8, and the oxygen content reaches 4mg/L;
(2)将沉降后的水依次引入二级净化系统河道、三级净化系统净水池塘和四级净化储水系统储水池塘;(2) The water after the settlement is introduced into the secondary purification system channel, the tertiary purification system water purification pond and the fourth purification water storage system water storage pond in turn;
(3)四级净化储水系统中水源进行水质监测,并将监测数据在显示屏上实时呈现,储存在四级净化储水系统中的水源经水泵引入到养殖池塘中;(3) The water source in the four-stage purification water storage system is monitored for water quality, and the monitoring data is displayed on the display screen in real time, and the water source stored in the four-stage purification water storage system is introduced into the aquaculture pond through the water pump;
(4)在高水位养殖池塘中放养斑点叉尾鮰,投放量为每亩1200尾,规格为100g/尾,放养青虾为10万尾/亩,放养规格为0.7cm,养殖水深为2.0m;在二级净化系统内放养规格为100g/尾的白鲢60尾/亩、鳙鱼50尾/亩;在河道底部放养螺蛳200kg/亩,在三级净化系统内种植空心菜、鱼腥草、10%浮叶植物、20%沉水植物和30%挺水植物,养殖水深为2.0m;在储水池塘内通过物联网管理系统实现对水质的实时在线检测;(4) Stocking channel catfish in high-water aquaculture ponds, the stocking amount is 1200 per mu, the size is 100g/tail, the stocking size of green shrimp is 100,000/mu, the stocking size is 0.7cm, and the breeding water depth is 2.0m; In the secondary purification system, 60 silver carp/mu and 50 bighead carp with a specification of 100g/tail are stocked; 200kg/mu of snails are stocked at the bottom of the river, and water spinach, Houttuynia cordata, 10% Floating-leaf plants, 20% submerged plants and 30% emergent plants, the culture depth is 2.0m; the real-time online detection of water quality is realized in the storage pond through the Internet of Things management system;
物联网系统主要由下位机、上位机以及App(虾易通)三部分组成。下位机包括主控CPU、传感器模块、无线通信模块、电源模块与电气设备模块等,实现数据的采集、发送以及下发指令的执行;上位机属于Windows系统的阿里云服务器,主要对下位机上传的数据进行存储、判断与下发控制下位机的指令;App(虾易通)运行于Android操作平台,主要进行数据的实时显示与过往数据追溯以及发出控制下位机设备的指令。The Internet of Things system is mainly composed of three parts: the lower computer, the upper computer and the App (Shrimp Yitong). The lower computer includes the main control CPU, sensor module, wireless communication module, power supply module and electrical equipment module, etc., to realize data collection, transmission and execution of issued instructions; the upper computer belongs to the Alibaba Cloud server of Windows system, which mainly uploads data to the lower computer. The data is stored, judged and issued to control the command of the lower computer; App (Shrimp Yitong) runs on the Android operating platform, mainly for the real-time display of data and the traceability of past data, as well as the command to control the lower computer equipment.
具体地,下位机负责完成水质参数的采集、处理、上传及控制各种执行机构的启停。水质参数主要由温度传感器、pH传感器、溶解氧传感器等采集完成;数据经无线通信模块上传;执行机构主要包括投饵机、水泵与增氧泵。Specifically, the lower computer is responsible for completing the collection, processing, uploading of water quality parameters and controlling the start and stop of various actuators. The water quality parameters are mainly collected by temperature sensors, pH sensors, dissolved oxygen sensors, etc.; the data is uploaded through the wireless communication module; the actuators mainly include feeders, water pumps and oxygen boosting pumps.
具体地,上位机负责将系统各个部分有机地串联到一起,其功能主要分为参数设置、数据通信、判断、存储、实时显示以及指令生成等部分。上位机软件使用C++语言在QtCreater平台进行开发。上位机数据处理包括三部分:上位机对下位机上传数据的处理,对App请求数据的处理以及转发App给下位机的指令。数据处理所需的阈值可通过界面中的警报参数设置功能进行设置。Specifically, the host computer is responsible for organically connecting all parts of the system together, and its functions are mainly divided into parameter setting, data communication, judgment, storage, real-time display, and command generation. The host computer software is developed on the QtCreater platform using C++ language. The data processing of the upper computer includes three parts: the processing of the data uploaded by the upper computer to the lower computer, the processing of the data requested by the App, and the instruction of forwarding the App to the lower computer. The thresholds required for data processing can be set through the alarm parameter setting function in the interface.
具体地,用虾易通查看养殖池塘水质pH值、溶解氧和温度值,并实现手机控制电气设备。虾易通的运行平台为安卓智能手机,主要完成下位机的远程控制、数据的实时浏览以及过往数据追溯等功能。具体操作流程见图6;Specifically, use Shrimp Yitong to check the pH value, dissolved oxygen and temperature value of the water quality of the aquaculture pond, and realize the control of electrical equipment by mobile phone. The operating platform of Shrimp Yitong is an Android smartphone, which mainly completes the functions of remote control of the lower computer, real-time browsing of data, and traceability of past data. The specific operation process is shown in Figure 6;
(5)将养殖池塘中的水排放到二级净化系统的河道中进行净化沉降;(5) the water in the culture pond is discharged into the river channel of the secondary purification system for purification and settlement;
(6)然后将沉降后的水依次引入三级净化系统和四级净化储水系统;(6) then introduce the settled water into the three-stage purification system and the four-stage purification water storage system successively;
(7)四级净化储水系统中水源进行水质监测,并将监测数据在显示屏上实时呈现,储存在四级净化储水系统中的水源引入到养殖池塘中实现综合套养循环养殖。(7) The water source in the four-stage purification water storage system is monitored for water quality, and the monitoring data is displayed on the display screen in real time. The water source stored in the four-stage purification water storage system is introduced into the aquaculture pond to realize the comprehensive set of culture and circulating aquaculture.
养殖结果:经过一年养殖,单产收益斑点叉尾鮰鱼2200斤,鲢鱼、鳙鱼单产900斤,水生植物400斤,青虾200斤,螺蛳1000斤,菱角400斤。根据市场现有价值计算,收益约在7500元/亩,经济收益较比技术改革之前的收益增长40-50%。Breeding results: After a year of cultivation, the yield per unit of channel catfish was 2200 jin, silver carp and bighead carp 900 jin, aquatic plants 400 jin, green shrimp 200 jin, snail 1000 jin and water chestnut 400 jin. Calculated according to the current market value, the income is about 7,500 yuan/mu, and the economic income has increased by 40-50% compared with the income before the technological reform.
综上,采用本发明实施例的养殖模式和方法,一方面可减少人力投入,减少养殖管理成本;另一方面,避免了养殖尾水的排放,基本可以做到“零排放”,节约用水超过50%;第三方面,沉降、净化、储水池的综合利用可以带来更多的经济效益,水培的中草药和蔬菜可以达到1kg/m2,并且可以多次采摘,同时可以更有利于养殖水体的净化和养殖鱼类健康生长。此外,本发明与现有的常规养殖和现有循环水养殖相比,具有放养量大成活率高的优点,是一种“高效、优质、生态、健康、安全”的鱼虾共生的综合套养循环养殖模式,从而可以促进水产养殖产业的健康发展。To sum up, by adopting the breeding mode and method of the embodiment of the present invention, on the one hand, manpower input can be reduced, and the cost of breeding management can be reduced; 50%; thirdly, the comprehensive utilization of sedimentation, purification and storage tanks can bring more economic benefits. The hydroponic Chinese herbs and vegetables can reach 1kg/m 2 , and can be picked multiple times, which is more conducive to breeding. Purification of water bodies and healthy growth of farmed fish. In addition, compared with the existing conventional culture and the existing circulating water culture, the present invention has the advantages of large stocking amount and high survival rate, and is a comprehensive set of "efficient, high-quality, ecological, healthy and safe" fish and shrimp symbiosis. It can promote the healthy development of the aquaculture industry.
上述对实施例的描述是为了便于该技术领域的普通技术人员能理解和使用本发明。熟悉本领域技术人员显然可以容易的对这些实施例做出各种修改,并把在此说明的一般原理应用到其他实施例中,而不必经过创造性的劳动。因此,本发明不限于上述实施例。本领域技术人员根据本发明的原理,不脱离本发明的范畴所做出的改进和修改都应该在本发明的保护范围之内。The foregoing description of the embodiments is provided to facilitate understanding and use of the present invention by those of ordinary skill in the art. It will be apparent to those skilled in the art that various modifications to these embodiments can be readily made, and the general principles described herein can be applied to other embodiments without inventive effort. Therefore, the present invention is not limited to the above-described embodiments. Improvements and modifications made by those skilled in the art according to the principles of the present invention without departing from the scope of the present invention should all fall within the protection scope of the present invention.
Claims (7)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010826074.6A CN111919808A (en) | 2020-08-17 | 2020-08-17 | Comprehensive fish and shrimp breeding purification system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010826074.6A CN111919808A (en) | 2020-08-17 | 2020-08-17 | Comprehensive fish and shrimp breeding purification system |
Publications (1)
Publication Number | Publication Date |
---|---|
CN111919808A true CN111919808A (en) | 2020-11-13 |
Family
ID=73311049
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202010826074.6A Pending CN111919808A (en) | 2020-08-17 | 2020-08-17 | Comprehensive fish and shrimp breeding purification system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN111919808A (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112674000A (en) * | 2020-12-18 | 2021-04-20 | 巨大(江苏)农业科技有限公司 | Prawn ecological breeding and polyculture method based on facility microalgae culture |
CN113159626A (en) * | 2021-05-13 | 2021-07-23 | 广东河海生态环境技术有限公司 | Submerged plant-complex flora combined immobilized microorganism technology |
CN113749033A (en) * | 2021-07-28 | 2021-12-07 | 河海大学 | Intelligent control device and method for water circulation of modular aquaculture farm |
CN114451337A (en) * | 2022-02-24 | 2022-05-10 | 浙江春归雁生态农业科技有限公司 | Method for breeding Scylla paramamosain in pond by saline-alkali water in inner Mongolia plateau saline-alkali soil |
CN114766343A (en) * | 2022-05-10 | 2022-07-22 | 济宁四丰农业科技有限公司 | Vegetable cultivation and nutrition supply device and cultivation method |
CN114766396A (en) * | 2022-05-06 | 2022-07-22 | 广东越群生物科技股份有限公司 | Nutrition strengthening method for promoting development of young red east star spot fish |
CN116508711A (en) * | 2023-06-05 | 2023-08-01 | 武汉中科水生生态环境股份有限公司 | Concentrated continuous cultivation tail water multi-circulation treatment system |
Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6447681B1 (en) * | 2000-08-07 | 2002-09-10 | Kent Sea Tech Corporation | Aquaculture wastewater treatment system and method of making same |
CN101120661A (en) * | 2007-09-13 | 2008-02-13 | 中国科学院水生生物研究所 | A device and method for ecological fish farming based on composite vertical flow artificial wetland |
US20090178623A1 (en) * | 2008-01-08 | 2009-07-16 | Ford Derek B | Vivarium and filtration system |
CN102124972A (en) * | 2011-02-18 | 2011-07-20 | 山东省淡水水产研究所 | Fresh water scale pond ecological breeding system |
CN103070130A (en) * | 2013-01-30 | 2013-05-01 | 中国水产科学研究院淡水渔业研究中心 | System and method for purifying and circularly utilizing water in fish aquaculture pond |
CN103663710A (en) * | 2013-12-12 | 2014-03-26 | 南京大学 | Vertical-flow self-aeration annular artificial wetland system |
CN110558257A (en) * | 2019-10-09 | 2019-12-13 | 江苏省渔业技术推广中心 | method for carrying out comprehensive culture of channel catfish in pond industrialized system |
CN110934096A (en) * | 2019-12-10 | 2020-03-31 | 山西省水产育种养殖科学实验中心 | Bicarbonate saline-alkali land pond circulating water ecological breeding system and method |
-
2020
- 2020-08-17 CN CN202010826074.6A patent/CN111919808A/en active Pending
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6447681B1 (en) * | 2000-08-07 | 2002-09-10 | Kent Sea Tech Corporation | Aquaculture wastewater treatment system and method of making same |
CN101120661A (en) * | 2007-09-13 | 2008-02-13 | 中国科学院水生生物研究所 | A device and method for ecological fish farming based on composite vertical flow artificial wetland |
US20090178623A1 (en) * | 2008-01-08 | 2009-07-16 | Ford Derek B | Vivarium and filtration system |
CN102124972A (en) * | 2011-02-18 | 2011-07-20 | 山东省淡水水产研究所 | Fresh water scale pond ecological breeding system |
CN103070130A (en) * | 2013-01-30 | 2013-05-01 | 中国水产科学研究院淡水渔业研究中心 | System and method for purifying and circularly utilizing water in fish aquaculture pond |
CN103663710A (en) * | 2013-12-12 | 2014-03-26 | 南京大学 | Vertical-flow self-aeration annular artificial wetland system |
CN110558257A (en) * | 2019-10-09 | 2019-12-13 | 江苏省渔业技术推广中心 | method for carrying out comprehensive culture of channel catfish in pond industrialized system |
CN110934096A (en) * | 2019-12-10 | 2020-03-31 | 山西省水产育种养殖科学实验中心 | Bicarbonate saline-alkali land pond circulating water ecological breeding system and method |
Non-Patent Citations (1)
Title |
---|
雷旭: "复合垂直流人工湿地-循环水养殖系统微生物群落的结构分析", 《中国优秀博硕士学位论文全文数据库(硕士) 农业科技辑》 * |
Cited By (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112674000A (en) * | 2020-12-18 | 2021-04-20 | 巨大(江苏)农业科技有限公司 | Prawn ecological breeding and polyculture method based on facility microalgae culture |
CN112674000B (en) * | 2020-12-18 | 2022-03-29 | 巨大(江苏)农业科技有限公司 | Prawn ecological breeding and polyculture method based on facility microalgae culture |
CN113159626A (en) * | 2021-05-13 | 2021-07-23 | 广东河海生态环境技术有限公司 | Submerged plant-complex flora combined immobilized microorganism technology |
CN113159626B (en) * | 2021-05-13 | 2021-11-26 | 广东河海生态环境有限公司 | Submerged plant-complex flora combined immobilized microorganism system |
CN113749033A (en) * | 2021-07-28 | 2021-12-07 | 河海大学 | Intelligent control device and method for water circulation of modular aquaculture farm |
CN114451337A (en) * | 2022-02-24 | 2022-05-10 | 浙江春归雁生态农业科技有限公司 | Method for breeding Scylla paramamosain in pond by saline-alkali water in inner Mongolia plateau saline-alkali soil |
CN114766396A (en) * | 2022-05-06 | 2022-07-22 | 广东越群生物科技股份有限公司 | Nutrition strengthening method for promoting development of young red east star spot fish |
CN114766396B (en) * | 2022-05-06 | 2024-04-05 | 广东越群海洋生物科技股份有限公司 | Nutrient enrichment method for promoting development of juvenile red east macula |
CN114766343A (en) * | 2022-05-10 | 2022-07-22 | 济宁四丰农业科技有限公司 | Vegetable cultivation and nutrition supply device and cultivation method |
CN114766343B (en) * | 2022-05-10 | 2023-04-07 | 济宁四丰农业科技有限公司 | Vegetable cultivation and nutrition supply device and cultivation method |
CN116508711A (en) * | 2023-06-05 | 2023-08-01 | 武汉中科水生生态环境股份有限公司 | Concentrated continuous cultivation tail water multi-circulation treatment system |
CN116508711B (en) * | 2023-06-05 | 2024-03-19 | 武汉中科水生生态环境股份有限公司 | Concentrated continuous cultivation tail water multi-circulation treatment system |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN111919808A (en) | Comprehensive fish and shrimp breeding purification system | |
CN104855310B (en) | Acrossocheilus fasciatus simulated ecological factory large scale breeding and domestication method | |
CN108967085B (en) | Rice field-south america white shrimp dystopy ecological breeding system | |
CN106234270B (en) | A method of circulation flowing water fish farming system cultivates Penaeus Vannmei | |
CN107258651A (en) | A kind of stereo ecological cultivating system of control body eutrophication | |
CN105941289B (en) | A high-efficiency and low-pollution greenhouse soft-shelled turtle breeding system and a method for recycling breeding wastewater | |
AU2020103871A4 (en) | A self-purification system for crab pond aquaculture with air stripping and water retracing flowing around the whole pond | |
CN106417114B (en) | River snail, black carp Collocation cultivation improve the ecological environmental-protection cultivation method of black carp yield | |
CN104585081A (en) | Underground water circulation water-saving type sturgeon ecological breeding method | |
CN113213710A (en) | Seawater factory greenhouse aquaculture penaeus vannamei tail water treatment system and method | |
CN112352715A (en) | Facility and method for large-scale culture of perinereis aibuhitensis by using prawn culture wastewater | |
CN110250062B (en) | Method for comprehensively utilizing seawater | |
CN102106326A (en) | Method for three-dimensional and artificial seedlings cultivation of perinereis aibuhitensis | |
CN1460413A (en) | Method and device for breeding salmon | |
CN205233182U (en) | Crab shrimpfish circulation farming systems | |
CN1219430C (en) | Youngling of large sea horse and artificial cultivating method of commodity sea horse and its equipment | |
CN106804498B (en) | A high-density culture method of Neomysis orientalis in the culture pond of Portunus trituberculatus | |
CN206101318U (en) | Ecological fish farming system | |
CN109319939B (en) | A kind of artificial Lake Water Body complex ecological purification system | |
CN116076425A (en) | Fully-closed circulating water intensive culture system for prawns and culture method thereof | |
CN106259068B (en) | A kind of polyculture method of Holothuria scabra and Penaeus Vannmei tank interior | |
CN102060387A (en) | Method for treating polluted water body by using water hyacinths | |
CN104642089B (en) | A kind of polyculture method of fragrant plant mentioned in ancient texts and grouper | |
CN107509673A (en) | A kind of resource utilization method of intensive Environment of Litopenaeus vannamei Low breeding wastewater | |
CN1739345A (en) | High pond domestication and culture method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20201113 |