WO2021227534A1 - Biological combined purification pond for freshwater aquaculture tail water - Google Patents

Biological combined purification pond for freshwater aquaculture tail water Download PDF

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Publication number
WO2021227534A1
WO2021227534A1 PCT/CN2020/141237 CN2020141237W WO2021227534A1 WO 2021227534 A1 WO2021227534 A1 WO 2021227534A1 CN 2020141237 W CN2020141237 W CN 2020141237W WO 2021227534 A1 WO2021227534 A1 WO 2021227534A1
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pond
water
fish
treatment unit
tail
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PCT/CN2020/141237
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French (fr)
Chinese (zh)
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江兴龙
郭少鹏
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集美大学
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • C02F3/327Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae characterised by animals and plants
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • C02F3/322Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae use of algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2203/00Apparatus and plants for the biological treatment of water, waste water or sewage
    • C02F2203/006Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/08Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/10Solids, e.g. total solids [TS], total suspended solids [TSS] or volatile solids [VS]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/14NH3-N
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/16Total nitrogen (tkN-N)
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/14Maintenance of water treatment installations

Definitions

  • the invention specifically relates to a biological combined purification pond for freshwater aquaculture tail water.
  • the technical problem to be solved by the present invention is to provide a biological combined purification pond for freshwater aquaculture tail water, which solves the current problem of high investment and operating costs for nitrogen and phosphorus removal from aquaculture tail water, and has low investment and operating costs. Energy saving, no secondary pollution and easy management.
  • the present invention is realized as follows: a biological combined purification pond for freshwater aquaculture tail water, the biological combined purification pond includes a first-stage treatment unit pond, a second-stage treatment unit pond, the first-stage treatment unit pond, and a second-stage treatment unit pond.
  • the secondary treatment unit is connected to the pond.
  • the first-stage processing unit ponds are stocked with fishes of different feeding habits and different habitats.
  • the second-stage treatment unit pond is provided with aquatic plants and a biofilm water purification grid, and the seedling amount of the aquatic plant is 0.2 ⁇ 0.8kg/m2; the biofilm water purification grid is based on the pond water area per mu Set 5 ⁇ 20 groups.
  • the filter-feeding fish stocked in fingerlings per mu of water surface are as follows: 100-150 silver carp, 50-60 bighead carp, with an average size of 200-300g/tail; omnivorous fishes are as follows: carp 1600- 2000 fish, average size 100-150g/tail, crucian carp 1200-1500, average size 50-75g/tail; scraping fishes are as follows: carp 800-1200, average size 25-50g/tail; herbivorous fish : 200-250 grass carp, with an average size of 500-600g/tail.
  • the aquatic plant is a combination of Eichhornia crassipes or Eichhornia crassipes and Hydrilla verticillata, Valeriana spp, Myriophyllum spp, Ceratophyllum spp, Porphyra spp, and Elodea; each group of said biofilm net
  • the length of the water grid is 20-40m, the height is 0.7-1.4m, and the distance between each group of the biofilm water purification grid is not less than 1m.
  • the fishes can be harvested and released in rotation, that is, fishes that reach the market specifications are fished and marketed in an appropriate amount, while continuing to replenish the fish species to maintain the first-level treatment
  • the stock of fish in the unit pond is greater than the total weight of the initially stocked fingerlings.
  • the first-stage treatment unit pond is dredged with a mud suction pump every winter.
  • the present invention has the following advantages.
  • the invention solves the current problems of high investment and operation cost for nitrogen and phosphorus removal from aquaculture tail water, and has the advantages of low investment and operation costs, energy saving, no secondary pollution, simple management and the like.
  • the area of constructed wetland ⁇ 15% of the total pond culture area
  • the area is reduced (the area of the present invention ⁇ 10% of the total pond culture area)
  • the problem of secondary pollution caused by the release of nitrogen and phosphorus due to plant corruption can avoid the easy clogging of the substrate in the middle and late stages of the operation of the constructed wetland method, and the problem of secondary pollution caused by the release of nitrogen and phosphorus due to plant corruption.
  • the invention does not use chemical reagents, and avoids the problems of high operating cost and easy to cause secondary pollution in the chemical reagent precipitation method.
  • the technology of the present invention uses a biological combination purification method to construct a secondary treatment unit pond to treat the aquaculture tail water, so that the nitrogen, phosphorus and organic matter in the aquaculture tail water can be used by a variety of fishes, water hyacinth and other aquatic plants and The assimilation, transformation and degradation of biofilm bacteria, and the re-feeding and utilization of aquatic plants by grass carp, etc., and finally being marketed by fish products, thereby removing nitrogen, phosphorus and organic substances in the aquaculture tail water from the water and realizing the tail water The waste that pollutes the water body is finally transformed into high-quality aquatic animal protein for human consumption through the food chain and food web constructed by this technology.
  • the discharge of suspended solids, pH, ammonia nitrogen, total nitrogen, total phosphorus, permanganate index, BOD5, COD and other water quality indicators can meet the "Freshwater Pond Aquaculture Water Discharge Requirements" (SC/ T 9101-2007) the first-level discharge standard, or the national surface water third-class water standard, meets the environmental protection discharge requirements.
  • Figure 1 is a schematic diagram of a biological combined purification pond for freshwater aquaculture tail water according to the present invention.
  • Figure 2 is a side view of the second-stage treatment pond of the present invention.
  • the total weight of the storage pond is generally based on the expected total weight of fish and shrimp per 20-40 tons, with 1-1.5 acres of water surface, the pond depth of 2.0 meters, and aerators; mixed aquaculture of various fishes is carried out. Carry out the polyculture of ponds with multi-trophic levels, different feeding habits (filter feeding, omnivorous, scraping, herbivorous), and no feed for fish in different habitats.
  • the first-level treatment unit pond 1 puts filter-feeding fish (feeding on phytoplankton, zooplankton and organic particulate matter) per mu of water surface: silver carp (Hypophthalmichthys molitrix) 100-150, bighead carp (Hypophthalmichthys nobilis) 50-60, average size 200-300g/tail; omnivorous fish (feeding on residual bait, organic debris and benthic animals): carp (Cyprinus carpio) 1600 -2000 tails, average size 100-150g/ tail, crucian carp (Carassius auratus) 1200-1500, average size 50-75g/tail; scraping fish (feeding on residual bait, organic debris, organic particulate matter, adherent organisms and benthic organisms): carp (Distoechodon sp.
  • Xenocypris sp. (Such as Distoechodon compressus, Xenocypris davidi Bleeker, etc.) 800-1200, average size 25-50g/tail; herbivorous fish (feeding on residual bait, organic debris, plant ): Grass carp (Ctenopharyngodon idellus ) 200-250 tails, average specification 500-600g/tail.
  • the freshwater aquaculture tail water that needs to be treated first flows into the first-stage treatment pond 1 for treatment.
  • the residual bait, feces and organic particles in the tail water can be stocked omnivorous fish (carp, crucian carp), herbivorous Fish (grass carp), filter-feeding fish (silver carp, bighead carp) and scraping fish (silver carp) eat food.
  • the dissolved nitrogen and phosphorus in the tail water can be absorbed and assimilated by phytoplankton, phytoplankton and zooplankton. It can also be ingested and used by fish.
  • the residual bait in the tail water, the organic particulate matter in the feces, the organic suspended matter, the soluble nitrogen and phosphorus, etc. can be ingested by fish or used indirectly, thereby being removed in large quantities.
  • some suspended matter and large particulate matter in the aquaculture tail water also precipitated and settled at the bottom of the pond.
  • the treated water flows from the upper water outlet 11 of the first-stage treatment pond 1 to the water inlet 21 of the second-stage treatment unit pond 2 by itself.
  • the general fish species can be reared for 6-10 months after the stocking, that is, depending on the situation, the fish of the larger size can be fished and marketed in an appropriate amount.
  • the fish species must be kept in the pond.
  • the stock of fish is greater than the total weight of the initial stocked fish species.
  • a batch of larger grass carp (with an average tail weight of more than 1kg grass carp) can be restocked in an appropriate amount to fully eat water hyacinths and other aquatic plants taken from the pond of the second-level treatment unit.
  • the mud suction pump is used to moderately dredge the silt every winter, and the silt can be accumulated on the pond ridge or transported for agricultural planting.
  • second-level treatment unit pond 2 aquatic plants 22 + biofilm water purification grid 23 combined ecological pond.
  • aquatic plants 22 + biofilm water purification grid 23 combination ecological ponds to synergistically remove nitrogen and phosphorus the ponds can be single or 2 ⁇ 3 ponds in parallel or in series.
  • the expected total weight of fish and shrimp storage ponds during the peak period of the breeding farm 1.2-2.0 acres of water surface and 1.5-2.0 meters of water depth are set for every 20-40 tons of expected output, and no aerator is equipped.
  • Planting water hyacinth (Eichhornia crassipes) and other aquatic plants according to the water area of the second-level treatment unit pond 2 Plant water hyacinth (more than 70%), with Hydrilla verticillata (Hydrilla verticillata), Vallisneria (Vallisneria nuttallii). sp.), Myriophyllum sp., Ceratophyllum sp., Potamogeton sp., Elodea nuttallii.
  • biofilm water purification grid 23 Set up biofilm water purification grid 23 according to the water area of the pond 2 of the second-level treatment unit, and set 5-20 groups of biofilm water purification grid 23 per mu, each group is 20m in length and 0.7-1.4m in height.
  • the biofilm water purification grid 23 is vertically suspended from about 20cm below the water surface of the pond.
  • the upper and lower nylon ropes 24 at both ends of the biofilm water purification grid 23 can be fixed in the pond by wooden stakes (steel piles) 25.
  • the rope is tied with a float (using foam plastic, etc.) every 3 ⁇ 5m to provide buoyancy (the buoyancy of a single float is 6 ⁇ 10kg), and the spacing between each group of biofilm water purification grids 23 arranged horizontally is not less than 1m.
  • the biofilm water purification grid can form a large area of biofilm and also absorb suspended solids in the water; use the huge amount of bacteria on the biofilm (including nitrifying bacteria, denitrifying bacteria, phosphorus accumulating bacteria and other heterotrophic bacteria) Bacteria, etc.) Carry out the assimilation, transformation and degradation of nitrogen, phosphorus and COD in water.
  • a large number of denitrifying bacteria on the biofilm can not only use the organic matter in the water body, but also use the organic carbon (organic acid, etc.) secreted by the roots of water hyacinth and other aquatic plants, and the decomposition of water plants such as water hyacinth.
  • the organic matter undergoes a denitrification reaction, so that the nitrate nitrogen in the water finally forms nitrogen, which is emitted from the water body, further reducing the concentration of nitrate nitrogen and total nitrogen in the water.
  • aquatic plants such as water hyacinths that have grown too densely can be manually salvaged every week and placed in the pond of the first-level treatment unit for feeding and reusing the cultivated grass carp to control the water hyacinths.
  • Reasonable growth density of lotus and other aquatic plants From November to March of the following year, water hyacinths and other aquatic plants whose stems and leaves start to turn yellow are usually salvaged every week and put into the pond of the first-level treatment unit to feed the cultivated grass carp to prevent water hyacinths and other aquatic plants A large amount of death and corruption release the nitrogen and phosphorus contained in the water.
  • the present invention mainly constructs a secondary tail water treatment unit pond to treat the culture tail water, and the culture tail water flows into the first level treatment unit pond, and uses a variety of polyculture fish to fully consume the residual bait and organic debris in the culture tail water.
  • the phytoplankton, zooplankton and benthic organisms formed after the waste water, fish manure and dissolved nitrogen and phosphorus in the tail water, and the formation of fertile water.
  • the tail water after the primary treatment then flows into the pond of the secondary treatment unit.
  • the established aquatic plant + biofilm water purification grid combination ecological pond is used to further treat the dissolved nitrogen and phosphorus, COD and suspended solids in the water.
  • the constructed biological combination purification pond of freshwater aquaculture tail water is used for advanced treatment of nitrogen, phosphorus and organic matter in eel aquaculture tail water.
  • the result data is as follows.
  • Influent refers to the aquaculture tail water
  • effluent refers to the discharged water after treatment in the treatment tank.
  • the discharged water after aquaculture tail water is treated by a biological combination purification pond of freshwater aquaculture tail water constructed by the present invention, its ammonia nitrogen, total nitrogen, total phosphorus, permanganate index, BOD5 and COD, etc. It meets the Class III water quality standard in the National Environmental Quality Standard for Surface Water (GB3838-2002), and also meets the first level discharge standard specified in the Freshwater Pond Aquaculture Water Discharge Requirements (SC/T 9101-2007). It shows that the secondary treatment unit pond constructed by the application of the biological combined purification method of the present invention has good denitrification, phosphorus removal and organic matter degradation capabilities.

Abstract

A biological combined purification pond for freshwater aquaculture tail water. The pond comprises a first-stage treatment unit pond (1) and a second-stage treatment unit pond (2), wherein the first-stage treatment unit pond (1) and the second-stage treatment unit pond (2) are connected. Fish, which have different feeding habits and inhabit different water layers, are released into the first-stage treatment unit pond (1), with the types of the fish and the released mass ratio thereof being as follows: filter-feeding fishes : omnivorous fishes : detritivorous fishes : herbivorous fishes = (0.8-0.9) : 6.0 : (0.5-0.9) : (2.7-2.2). Aquatic plants (22) and biological membrane water purification bars (23) are provided in the second-stage treatment unit pond (2); the seedling adding amount of the aquatic plants (22) being 0.2-0.8 kg/m2; and 5-20 groups of biological membrane water purification bars (23) being provided per mu according to the water surface area of the pond.

Description

一种淡水养殖尾水的生物组合净化塘Biological combination purification pond for freshwater aquaculture tail water 技术领域Technical field
本发明具体涉及一种淡水养殖尾水的生物组合净化塘。The invention specifically relates to a biological combined purification pond for freshwater aquaculture tail water.
背景技术Background technique
我国是水产养殖大国,养殖产量约占世界养殖产量的68%,其中,池塘养殖产量约占45%。但池塘养殖尾水和工厂化养殖尾水都基本未经处理直接排放,由于养殖尾水中一般都含有较高的氮和磷,导致了对周边水域环境不同程度的富营养化污染。为保护水域生态环境,使排放水的水质能符合国家的相关环保要求,如符合《淡水池塘养殖水排放要求》(SC/T 9101-2007)、国家《地表水环境质量标准》(GB3838-2002)中的Ⅲ类水质标准等。当前的池塘养殖尾水或工厂化养殖尾水处理技术,主要采用人工湿地技术、生态塘技术及综合应用化学辅助除磷技术。但是,人工湿地技术存在占地面积大,运行中后期容易发生基质堵塞、植物腐败产生二次污染及处理效果下降影响出水水质等问题;生态塘技术存在占地面积大,处理效果变化幅度较大,出水水质较不稳定等问题;化学试剂辅助除磷技术也存在占地面积大,运行成本较高、处理效果稳定性较差及容易导致二次污染等问题。许多水产养殖场因受土地面积限制和处理成本高的问题,未能开展尾水排放处理,污染了周边水域环境或面临因环保不达标而被强制停产的问题。my country is a large aquaculture country, with aquaculture production accounting for about 68% of the world's aquaculture production, of which, pond aquaculture production accounts for about 45%. However, the tail water of pond culture and the tail water of factory farming are basically discharged directly without treatment. Because the tail water of aquaculture generally contains high nitrogen and phosphorus, it has caused different degrees of eutrophication pollution to the surrounding water environment. In order to protect the ecological environment of the water area, the water quality of the discharged water can meet the relevant national environmental protection requirements, such as the "Freshwater Pond Aquaculture Water Discharge Requirements" (SC/T 9101-2007), the national "Surface Water Environmental Quality Standards" (GB3838-2002) ) Class III water quality standards, etc. Current pond farming tail water or factory farming tail water treatment technology mainly adopts artificial wetland technology, ecological pond technology and comprehensive application of chemically assisted phosphorus removal technology. However, the constructed wetland technology has a large area, and it is prone to substrate clogging in the middle and late stages of operation, secondary pollution caused by plant decay, and reduced treatment effects that affect the quality of the effluent; ecological pond technology has a large area, and the treatment effect varies greatly. , The effluent water quality is relatively unstable and other problems; the chemical reagent-assisted phosphorus removal technology also has problems such as large area, high operating cost, poor stability of the treatment effect, and easy to cause secondary pollution. Many aquaculture farms have failed to carry out tail water discharge treatment due to land area restrictions and high treatment costs, polluting the surrounding water environment or facing the problem of forced suspension of production due to non-compliance with environmental protection standards.
技术问题technical problem
本发明要解决的技术问题,在于提供一种淡水养殖尾水的生物组合净化塘,解决了当前水产养殖尾水脱氮除磷投资与运行成本较高的问题,具有投资和运行成本较低,节能,不产生二次污染和管理简便等优点。The technical problem to be solved by the present invention is to provide a biological combined purification pond for freshwater aquaculture tail water, which solves the current problem of high investment and operating costs for nitrogen and phosphorus removal from aquaculture tail water, and has low investment and operating costs. Energy saving, no secondary pollution and easy management.
技术解决方案Technical solutions
本发明是这样实现的:一种淡水养殖尾水的生物组合净化塘,所述生物组合净化塘包括第一级处理单元池塘、第二级处理单元池塘,所述第一级处理单元池塘、第二级处理单元池塘相连。The present invention is realized as follows: a biological combined purification pond for freshwater aquaculture tail water, the biological combined purification pond includes a first-stage treatment unit pond, a second-stage treatment unit pond, the first-stage treatment unit pond, and a second-stage treatment unit pond. The secondary treatment unit is connected to the pond.
所述第一级处理单元池塘内投放有不同食性和不同栖息水层鱼类,所述鱼类的种类及其投放质量比如下:滤食性鱼类:杂食性鱼类:刮食性鱼类:草食性鱼类 = 0.8-0.9:6.0:0.5-0.9:2.7-2.2。The first-stage processing unit ponds are stocked with fishes of different feeding habits and different habitats. The types of the fishes and their stock quality are as follows: filter-feeding fish: omnivorous fish: scraping fish: herbivorous fish Sex fish = 0.8-0.9: 6.0: 0.5-0.9: 2.7-2.2.
所述第二级处理单元池塘内设置有水生植物和生物膜净水栅,所述水生植物的种苗投放量为0.2~0.8kg/m2;所述生物膜净水栅按池塘水面积每亩设置5~20组。The second-stage treatment unit pond is provided with aquatic plants and a biofilm water purification grid, and the seedling amount of the aquatic plant is 0.2~0.8kg/m2; the biofilm water purification grid is based on the pond water area per mu Set 5~20 groups.
进一步地,按每亩水面,投放鱼种中的滤食性鱼类如下:鲢鱼100-150尾、鳙鱼50-60尾,平均规格200-300g/尾;杂食性鱼类如下:鲤鱼1600-2000尾、平均规格100-150g/尾,鲫鱼1200-1500尾、平均规格50-75g/尾;刮食性鱼类如下:鲴鱼800-1200尾、平均规格25-50g/尾;草食性鱼类:草鱼200-250尾,平均规格500-600g/尾。Furthermore, the filter-feeding fish stocked in fingerlings per mu of water surface are as follows: 100-150 silver carp, 50-60 bighead carp, with an average size of 200-300g/tail; omnivorous fishes are as follows: carp 1600- 2000 fish, average size 100-150g/tail, crucian carp 1200-1500, average size 50-75g/tail; scraping fishes are as follows: carp 800-1200, average size 25-50g/tail; herbivorous fish : 200-250 grass carp, with an average size of 500-600g/tail.
进一步地,所述水生植物为凤眼莲或凤眼莲与轮叶黑藻、苦草属、狐尾藻属、金鱼藻属、眼子菜属、伊乐藻的组合;每组所述生物膜净水栅的长度为20-40m、高度0.7~1.4m,且每组所述生物膜净水栅之间的间距不小于1m。Further, the aquatic plant is a combination of Eichhornia crassipes or Eichhornia crassipes and Hydrilla verticillata, Valeriana spp, Myriophyllum spp, Ceratophyllum spp, Porphyra spp, and Elodea; each group of said biofilm net The length of the water grid is 20-40m, the height is 0.7-1.4m, and the distance between each group of the biofilm water purification grid is not less than 1m.
进一步地,鱼种投放后经6-10个月的养殖,可进行轮捕轮放,即对达到上市规格的鱼类进行适量捕捞上市,同时继续补充投放鱼种,维持所述第一级处理单元池塘中的存鱼量大于初始投放的鱼种总重量。Furthermore, after 6-10 months of breeding of the fish species, the fishes can be harvested and released in rotation, that is, fishes that reach the market specifications are fished and marketed in an appropriate amount, while continuing to replenish the fish species to maintain the first-level treatment The stock of fish in the unit pond is greater than the total weight of the initially stocked fingerlings.
进一步地,在7-10月,每周对生长过密的水生植物进行打捞,并投放至第一级处理单元池塘,用于投喂草食性鱼类,以控制水生植物的生长密度。Further, from July to October, the densely growing aquatic plants are salvaged every week and put into the first-level treatment unit pond for feeding herbivorous fishes to control the growth density of aquatic plants.
进一步地,在11月到次年3月,每周对茎叶开始发黄的水生植物进行打捞,并投放至第一级处理单元池塘,用于投喂草食性鱼类。Furthermore, from November to March of the following year, the aquatic plants whose stems and leaves begin to turn yellow are salvaged every week and put into the pond of the first-level treatment unit for feeding herbivorous fish.
进一步地,于11月,补充投放一批平均尾重大于1kg的食草性鱼类,以充分摄食从第二级处理单元池塘中捞出的水生植物。Furthermore, in November, a batch of herbivorous fishes with an average tail weight of more than 1 kg was added to feed the aquatic plants recovered from the pond of the second-stage treatment unit.
进一步地,每年冬季用吸泥泵对第一级处理单元池塘进行清淤。Furthermore, the first-stage treatment unit pond is dredged with a mud suction pump every winter.
有益效果Beneficial effect
本发明具有如下优点。The present invention has the following advantages.
本发明解决了当前水产养殖尾水脱氮除磷投资与运行成本较高的问题,具有投资和运行成本较低,节能,不产生二次污染和管理简便等优点。与当前使用的人工湿地技术处理池塘养殖尾水(人工湿地占地面积≥池塘养殖总面积的15%)比较,减少了占地面积(本发明的占地面积≤池塘养殖总面积的10%),并能避免人工湿地法运行中后期基质易堵塞,植物腐败会产生氮磷释放二次污染的问题。The invention solves the current problems of high investment and operation cost for nitrogen and phosphorus removal from aquaculture tail water, and has the advantages of low investment and operation costs, energy saving, no secondary pollution, simple management and the like. Compared with the currently used constructed wetland technology to treat pond culture tail water (the area of constructed wetland ≥ 15% of the total pond culture area), the area is reduced (the area of the present invention ≤ 10% of the total pond culture area) , And can avoid the easy clogging of the substrate in the middle and late stages of the operation of the constructed wetland method, and the problem of secondary pollution caused by the release of nitrogen and phosphorus due to plant corruption.
本发明不使用化学试剂,避免了化学试剂沉淀法存在的运行费用高且容易造成二次污染的问题。本发明的技术,通过应用生物组合净化方法构建二级处理单元池塘处理养殖尾水,使养殖尾水中的氮磷和有机物质等,经多种鱼类的摄食利用、凤眼莲等水生植物和生物膜细菌等的同化、转化与降解,及水生植物被草鱼等的再摄食利用,最终经鱼产品捕捞上市,从而把养殖尾水中的氮磷和有机物质等从水中带出解除,实现尾水中污染水体的废弃物,通过本技术构建的食物链和食物网,最终转化为可供人类食用的优质水生动物蛋白质。养殖尾水经本技术处理后,可使悬浮物、pH、氨氮、总氮、总磷、高锰酸盐指数、BOD5、COD等水质指标的排放符合《淡水池塘养殖水排放要求》( SC/T 9101-2007)规定的一级排放标准,或国家地表水三类水标准,符合环保的排放要求。The invention does not use chemical reagents, and avoids the problems of high operating cost and easy to cause secondary pollution in the chemical reagent precipitation method. The technology of the present invention uses a biological combination purification method to construct a secondary treatment unit pond to treat the aquaculture tail water, so that the nitrogen, phosphorus and organic matter in the aquaculture tail water can be used by a variety of fishes, water hyacinth and other aquatic plants and The assimilation, transformation and degradation of biofilm bacteria, and the re-feeding and utilization of aquatic plants by grass carp, etc., and finally being marketed by fish products, thereby removing nitrogen, phosphorus and organic substances in the aquaculture tail water from the water and realizing the tail water The waste that pollutes the water body is finally transformed into high-quality aquatic animal protein for human consumption through the food chain and food web constructed by this technology. After the aquaculture tail water is treated with this technology, the discharge of suspended solids, pH, ammonia nitrogen, total nitrogen, total phosphorus, permanganate index, BOD5, COD and other water quality indicators can meet the "Freshwater Pond Aquaculture Water Discharge Requirements" (SC/ T 9101-2007) the first-level discharge standard, or the national surface water third-class water standard, meets the environmental protection discharge requirements.
附图说明Description of the drawings
下面参照附图结合实施例对本发明作进一步的说明。Hereinafter, the present invention will be further described with reference to the accompanying drawings and embodiments.
图1为本发明一种淡水养殖尾水的生物组合净化塘的示意图。Figure 1 is a schematic diagram of a biological combined purification pond for freshwater aquaculture tail water according to the present invention.
图2为本发明的第二级处理池塘的侧视图。Figure 2 is a side view of the second-stage treatment pond of the present invention.
本发明的实施方式Embodiments of the present invention
以下结合具体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 specific embodiments.
实施例。Examples.
1、参阅图1,第一级处理单元池塘1,各型鱼类组合混养净化塘;池塘可为单个或2~3个并联组合,按拟处理尾水养殖场预期的养殖高峰期鱼虾存塘总重量,一般按每20-40吨鱼虾预期存塘总重量,设置1-1.5亩水面,池塘水深2.0米,配置增氧机;开展多种鱼类混养殖。开展池塘多营养层级、不同食性(滤食性、杂食性、刮食性、草食性)和不同栖息水层鱼类的不投喂饲料的混养。1. Refer to Figure 1, the first-level treatment unit pond 1, and various types of fish combination polyculture purification pond; the pond can be a single or 2~3 parallel combination, according to the proposed treatment of tail water farms expected fish and shrimp breeding peak period The total weight of the storage pond is generally based on the expected total weight of fish and shrimp per 20-40 tons, with 1-1.5 acres of water surface, the pond depth of 2.0 meters, and aerators; mixed aquaculture of various fishes is carried out. Carry out the polyculture of ponds with multi-trophic levels, different feeding habits (filter feeding, omnivorous, scraping, herbivorous), and no feed for fish in different habitats.
(1)第一级处理单元池塘1按每亩水面,投放滤食性鱼类(摄食浮游植物、浮游动物和有机颗粒物):鲢鱼(Hypophthalmichthys molitrix )100-150尾、鳙鱼(Hypophthalmichthys nobilis )50-60尾,平均规格200-300g/尾;杂食性鱼类(摄食残饵、有机碎屑和底栖动物):鲤鱼(Cyprinus carpio)1600-2000尾、平均规格100-150g/尾,鲫鱼(Carassius auratus)1200-1500尾、平均规格50-75g/尾;刮食性鱼类(摄食残饵、有机碎屑、有机颗粒物、附着性生物和底栖生物):鲴鱼(Distoechodon sp. 或 Xenocypris sp.)(如扁圆吻鲴(Distoechodon compressus)、黄尾密鲴(Xenocypris davidi Bleeker)等)800-1200尾、平均规格25-50g/尾;草食性鱼类(摄食残饵、有机碎屑、植物):草鱼(Ctenopharyngodon idellus )200-250尾、平均规格500-600g/尾。(1) The first-level treatment unit pond 1 puts filter-feeding fish (feeding on phytoplankton, zooplankton and organic particulate matter) per mu of water surface: silver carp (Hypophthalmichthys molitrix) 100-150, bighead carp (Hypophthalmichthys nobilis) 50-60, average size 200-300g/tail; omnivorous fish (feeding on residual bait, organic debris and benthic animals): carp (Cyprinus carpio) 1600 -2000 tails, average size 100-150g/ tail, crucian carp (Carassius auratus) 1200-1500, average size 50-75g/tail; scraping fish (feeding on residual bait, organic debris, organic particulate matter, adherent organisms and benthic organisms): carp (Distoechodon sp. or Xenocypris sp. ) (Such as Distoechodon compressus, Xenocypris davidi Bleeker, etc.) 800-1200, average size 25-50g/tail; herbivorous fish (feeding on residual bait, organic debris, plant ): Grass carp (Ctenopharyngodon idellus ) 200-250 tails, average specification 500-600g/tail.
(2)混养鱼类的种类以及投放质量比例如下:滤食性鱼类:杂食性鱼类:刮食性鱼类:草食性鱼类 = 0.8-0.9:6.0:0.5-0.9:2.7-2.2。(2) The types of polyculture fish and the ratio of stock quality are as follows: filter-feeding fish: omnivorous fish: scraper fish: herbivorous fish = 0.8-0.9: 6.0: 0.5-0.9: 2.7-2.2.
(3)对投放的鱼类均不进行人工投饵,以充分摄食养殖尾水中的残饵、有机碎屑、有机颗粒物,及尾水中的鱼类粪便及溶解性氮磷等肥水后形成的浮游植物、浮游动物和底栖生物等。(3) No artificial bait is used for the fish to be fed, so as to fully ingest the residual bait, organic debris, organic particles in the tail water, and the plankton formed by the fertile water such as fish manure and dissolved nitrogen and phosphorus in the tail water. Plants, zooplankton and benthic organisms, etc.
(4)运行原理:需要处理的淡水养殖尾水首先流入第一级处理池塘1处理,尾水中的残饵、粪便和有机颗粒物,可被放养的杂食性鱼类(鲤鱼、鲫鱼)、草食性鱼类(草鱼)、滤食性鱼类(鲢鱼、鳙鱼)和刮食性鱼类(鲴鱼)等摄食,同时尾水中的溶解性氮磷可为浮游植物吸收同化利用,浮游植物和浮游动物又可为鱼类所摄食利用。因此,在第一级处理池塘1,尾水中的残饵、粪便中的有机颗粒物、有机悬浮物质、溶解性氮磷等,可为鱼类所摄食或间接利用,从而被大量去除。此外,养殖尾水中一些悬浮物质、大颗粒物质也发生沉淀作用,而沉降于池塘底部。经处理后的水从第一级处理池塘1的上部出水口11自流至第二级处理单元池塘2的进水口21。(4) Operation principle: The freshwater aquaculture tail water that needs to be treated first flows into the first-stage treatment pond 1 for treatment. The residual bait, feces and organic particles in the tail water can be stocked omnivorous fish (carp, crucian carp), herbivorous Fish (grass carp), filter-feeding fish (silver carp, bighead carp) and scraping fish (silver carp) eat food. At the same time, the dissolved nitrogen and phosphorus in the tail water can be absorbed and assimilated by phytoplankton, phytoplankton and zooplankton. It can also be ingested and used by fish. Therefore, in the first-stage treatment pond 1, the residual bait in the tail water, the organic particulate matter in the feces, the organic suspended matter, the soluble nitrogen and phosphorus, etc., can be ingested by fish or used indirectly, thereby being removed in large quantities. In addition, some suspended matter and large particulate matter in the aquaculture tail water also precipitated and settled at the bottom of the pond. The treated water flows from the upper water outlet 11 of the first-stage treatment pond 1 to the water inlet 21 of the second-stage treatment unit pond 2 by itself.
此外,一般鱼种投放后经6-10个月的养殖,可进行轮捕轮放,即视情况对达到较大规格的鱼类进行适量捕捞上市,同时继续补充投放鱼种,必须维持池塘中的存鱼量大于初始投放的鱼种总重量。于11月,可适量补充投放一批规格较大的草鱼(平均尾重大于1kg草鱼),以充分摄食从第二级处理单元池塘中捞出的凤眼莲等水生植物。每年冬季利用吸泥泵适度清淤,淤泥可堆积于池塘埂上或外运用于农业种植。In addition, the general fish species can be reared for 6-10 months after the stocking, that is, depending on the situation, the fish of the larger size can be fished and marketed in an appropriate amount. At the same time, the fish species must be kept in the pond. The stock of fish is greater than the total weight of the initial stocked fish species. In November, a batch of larger grass carp (with an average tail weight of more than 1kg grass carp) can be restocked in an appropriate amount to fully eat water hyacinths and other aquatic plants taken from the pond of the second-level treatment unit. The mud suction pump is used to moderately dredge the silt every winter, and the silt can be accumulated on the pond ridge or transported for agricultural planting.
    2. 参阅图1-2,第二级处理单元池塘2,水生植物22+生物膜净水栅23组合生态塘。通过建立水生植物22+生物膜净水栅23组合生态塘,协同脱氮除磷,池塘可为单个或2~3池并联或串联组合。按养殖场预期的养殖高峰期鱼虾存塘总重量,每20-40吨预期产量设置1.2-2.0亩水面,水深1.5-2.0米,不配置增氧机。2. Refer to Figure 1-2, second-level treatment unit pond 2, aquatic plants 22 + biofilm water purification grid 23 combined ecological pond. Through the establishment of aquatic plants 22 + biofilm water purification grid 23 combination ecological ponds to synergistically remove nitrogen and phosphorus, the ponds can be single or 2~3 ponds in parallel or in series. According to the expected total weight of fish and shrimp storage ponds during the peak period of the breeding farm, 1.2-2.0 acres of water surface and 1.5-2.0 meters of water depth are set for every 20-40 tons of expected output, and no aerator is equipped.
(1)按第二级处理单元池塘2水面积种植凤眼莲(Eichhornia crassipes)等水生植物,凤眼莲等水生植物22种苗初始投放量按0.2-0.8kg/m2估算投放总重量,主要种植凤眼莲(占比大于70%),搭配轮叶黑藻(Hydrilla verticillata)、苦草属(Vallisneria nuttallii)。 sp.)、狐尾藻属(Myriophyllum sp.)、金鱼藻属(Ceratophyllum sp.)、眼子菜属(Potamogeton sp.)、伊乐藻(Elodea nuttallii)。(1) Planting water hyacinth (Eichhornia crassipes) and other aquatic plants according to the water area of the second-level treatment unit pond 2 Plant water hyacinth (more than 70%), with Hydrilla verticillata (Hydrilla verticillata), Vallisneria (Vallisneria nuttallii). sp.), Myriophyllum sp., Ceratophyllum sp., Potamogeton sp., Elodea nuttallii.
(2)按第二级处理单元池塘2水面积设置生物膜净水栅23,每亩设置5-20组生物膜净水栅23,每组长度20m,高0.7~1.4m。将生物膜净水栅23从离池塘水面10下约20cm处垂直悬挂,生物膜净水栅23两端的上纲和下纲尼龙绳24可通过木桩(钢桩)25固定于池塘中,上纲绳每隔3~5m系1个浮子(可用泡沫塑料等)提供浮力(单个浮子的浮力6~10kg),横向设置的每组生物膜净水栅23之间的间距不小于1m。(2) Set up biofilm water purification grid 23 according to the water area of the pond 2 of the second-level treatment unit, and set 5-20 groups of biofilm water purification grid 23 per mu, each group is 20m in length and 0.7-1.4m in height. The biofilm water purification grid 23 is vertically suspended from about 20cm below the water surface of the pond. The upper and lower nylon ropes 24 at both ends of the biofilm water purification grid 23 can be fixed in the pond by wooden stakes (steel piles) 25. The rope is tied with a float (using foam plastic, etc.) every 3~5m to provide buoyancy (the buoyancy of a single float is 6~10kg), and the spacing between each group of biofilm water purification grids 23 arranged horizontally is not less than 1m.
(3)运行原理:(a)凤眼莲等水生植物通过大量同化吸收水中的氮磷而生长,也吸附水中的悬浮物;其根系中附着的大量细菌(含硝化细菌、反硝化细菌和聚磷菌等),及根系通过分泌氧和有机碳(有机酸等)也进一步促进了对氮磷及COD的同化、转化与降解。(3) Operation principle: (a) Eichhornia crassipes and other aquatic plants grow by assimilating a large amount of nitrogen and phosphorus in the water, and also absorb suspended solids in the water; a large number of bacteria (including nitrifying bacteria, denitrifying bacteria and polymerizing bacteria) are attached to their roots. Phosphate bacteria, etc.), and the roots secrete oxygen and organic carbon (organic acid, etc.), which further promote the assimilation, transformation and degradation of nitrogen, phosphorus and COD.
(b)设置的生物膜净水栅可形成大面积的生物膜,也吸附水中的悬浮物;利用生物膜上巨量的细菌(含硝化细菌、反硝化细菌、聚磷菌及其他的异养细菌等)开展对水中氮磷及COD的同化、转化与降解。(B) The biofilm water purification grid can form a large area of biofilm and also absorb suspended solids in the water; use the huge amount of bacteria on the biofilm (including nitrifying bacteria, denitrifying bacteria, phosphorus accumulating bacteria and other heterotrophic bacteria) Bacteria, etc.) Carry out the assimilation, transformation and degradation of nitrogen, phosphorus and COD in water.
(c)生物膜上大量的反硝化细菌,除了利用水体中的有机物外,还可利用凤眼莲等水生植物根系分泌的有机碳(有机酸等)及凤眼莲等水生植物死亡分解出的有机物,进行反硝化反应,使水中的硝酸盐氮最终形成氮气,从水体中散发出,进一步降低水中的硝酸盐氮和总氮浓度。(C) A large number of denitrifying bacteria on the biofilm can not only use the organic matter in the water body, but also use the organic carbon (organic acid, etc.) secreted by the roots of water hyacinth and other aquatic plants, and the decomposition of water plants such as water hyacinth. The organic matter undergoes a denitrification reaction, so that the nitrate nitrogen in the water finally forms nitrogen, which is emitted from the water body, further reducing the concentration of nitrate nitrogen and total nitrogen in the water.
此外,在7-10月,每周可对生长过量过密的凤眼莲等水生植物人工打捞投放至第一级处理单元池塘,用于投喂养殖的草鱼,进行再利用,以控制凤眼莲等水生植物的合理生长密度。11月到次年3月,一般每周对茎叶开始发黄的凤眼莲等水生植物打捞投放至第一级处理单元池塘,用于投喂养殖的草鱼,以防止凤眼莲等水生植物大量死亡腐败而把其含有的氮磷释放于水中。In addition, from July to October, aquatic plants such as water hyacinths that have grown too densely can be manually salvaged every week and placed in the pond of the first-level treatment unit for feeding and reusing the cultivated grass carp to control the water hyacinths. Reasonable growth density of lotus and other aquatic plants. From November to March of the following year, water hyacinths and other aquatic plants whose stems and leaves start to turn yellow are usually salvaged every week and put into the pond of the first-level treatment unit to feed the cultivated grass carp to prevent water hyacinths and other aquatic plants A large amount of death and corruption release the nitrogen and phosphorus contained in the water.
总之,本发明主要通过构建二级尾水处理单元池塘处理养殖尾水,养殖尾水流入第一级处理单元池塘,利用混养的多种鱼类,充分摄食养殖尾水中的残饵、有机碎屑、有机颗粒物,及尾水中的鱼类粪便及溶解性氮磷等肥水后形成的浮游植物、浮游动物和底栖生物等。经一级处理后的尾水然后流入第二级处理单元池塘,利用建立的水生植物+生物膜净水栅组合生态塘,进一步深度处理水中的溶解性氮磷、COD和悬浮物等,利用凤眼莲等水生植物大量同化吸收水中的氮磷,利用水生植物根系及生物膜上的大量细菌同化、转化与降解水中氮磷及COD。从而最终达到除磷脱氮、降解有机质和降低悬浮物浓度的效果。In short, the present invention mainly constructs a secondary tail water treatment unit pond to treat the culture tail water, and the culture tail water flows into the first level treatment unit pond, and uses a variety of polyculture fish to fully consume the residual bait and organic debris in the culture tail water. The phytoplankton, zooplankton and benthic organisms formed after the waste water, fish manure and dissolved nitrogen and phosphorus in the tail water, and the formation of fertile water. The tail water after the primary treatment then flows into the pond of the secondary treatment unit. The established aquatic plant + biofilm water purification grid combination ecological pond is used to further treat the dissolved nitrogen and phosphorus, COD and suspended solids in the water. A lot of aquatic plants such as ophthalmology assimilate and absorb nitrogen and phosphorus in the water, and utilize a large number of bacteria on the roots and biofilms of aquatic plants to assimilate, transform and degrade nitrogen, phosphorus and COD in the water. So as to finally achieve the effects of dephosphorization and denitrification, degradation of organic matter and reduction of suspended solids concentration.
3、实施效果。3. Implementation effect.
应用上述方法,构建的淡水养殖尾水的生物组合净化塘,对鳗鱼养殖尾水进行氮磷和有机质的深度处理,结果数据如下表。Using the above method, the constructed biological combination purification pond of freshwater aquaculture tail water is used for advanced treatment of nitrogen, phosphorus and organic matter in eel aquaculture tail water. The result data is as follows.
Figure 195873dest_path_image001
Figure 195873dest_path_image001
.
备注:进水指的是养殖尾水,出水指的是经处理池处理后的排放水。Remarks: Influent refers to the aquaculture tail water, and effluent refers to the discharged water after treatment in the treatment tank.
综上,养殖尾水经过应用本发明构建的一种淡水养殖尾水的生物组合净化塘处理后的排放水,其氨氮、总氮、总磷、高锰酸盐指数、BOD5和COD等都达到了国家《地表水环境质量标准》(GB3838-2002)中的Ⅲ类水质标准,也符合《淡水池塘养殖水排放要求》( SC/T 9101-2007)规定的一级排放标准。表明本发明应用生物组合净化方法构建的二级处理单元池塘具有良好的脱氮除磷及降解有机质的能力。In summary, the discharged water after aquaculture tail water is treated by a biological combination purification pond of freshwater aquaculture tail water constructed by the present invention, its ammonia nitrogen, total nitrogen, total phosphorus, permanganate index, BOD5 and COD, etc. It meets the Class III water quality standard in the National Environmental Quality Standard for Surface Water (GB3838-2002), and also meets the first level discharge standard specified in the Freshwater Pond Aquaculture Water Discharge Requirements (SC/T 9101-2007). It shows that the secondary treatment unit pond constructed by the application of the biological combined purification method of the present invention has good denitrification, phosphorus removal and organic matter degradation capabilities.
虽然以上描述了本发明的具体实施方式,但是熟悉本技术领域的技术人员应当理解,我们所描述的具体的实施例只是说明性的,而不是用于对本发明的范围的限定,熟悉本领域的技术人员在依照本发明的精神所作的等效的修饰以及变化,都应当涵盖在本发明的权利要求所保护的范围内。Although the specific embodiments of the present invention are described above, those skilled in the art should understand that the specific embodiments described by us are only illustrative, and are not used to limit the scope of the present invention. The equivalent modifications and changes made by the skilled person in accordance with the spirit of the present invention should be covered by the scope of protection of the claims of the present invention.

Claims (8)

  1. 一种淡水养殖尾水的生物组合净化塘,其特征在于:所述生物组合净化塘包括第一级处理单元池塘、第二级处理单元池塘,所述第一级处理单元池塘、第二级处理单元池塘相连;A biological combination purification pond for freshwater aquaculture tail water, characterized in that: the biological combination purification pond comprises a first-stage treatment unit pond, a second-stage treatment unit pond, the first-stage treatment unit pond, and a second-stage treatment unit pond. Unit ponds are connected;
    所述第一级处理单元池塘内投放有不同食性和不同栖息水层鱼类,所述鱼类的种类及其投放质量比如下:滤食性鱼类:杂食性鱼类:刮食性鱼类:草食性鱼类 = 0.8-0.9:6.0:0.5-0.9:2.7-2.2;The first-stage processing unit ponds are stocked with fishes of different feeding habits and different habitats. The types of the fishes and their stock quality are as follows: filter-feeding fish: omnivorous fish: scraping fish: herbivorous fish Sex fish = 0.8-0.9: 6.0: 0.5-0.9: 2.7-2.2;
    所述第二级处理单元池塘内设置有水生植物和生物膜净水栅,所述水生植物的种苗投放量为0.2~0.8kg/m 2;所述生物膜净水栅按池塘水面积每亩设置5~20组。 Pond the secondary processing unit is provided with a fresh water aquatic plants and biofilm gate, the delivery amount of aquatic plants seedlings 0.2 ~ 0.8kg / m 2; the biofilm pond water purifier according to the gate area per Set 5-20 groups per mu.
  2. 根据权利要求1所述的一种淡水养殖尾水的生物组合净化塘,其特征在于:按每亩水面,投放鱼种中的滤食性鱼类如下:鲢鱼100-150尾、鳙鱼50-60尾,平均规格200-300g/尾;杂食性鱼类如下:鲤鱼1600-2000尾、平均规格100-150g/尾,鲫鱼1200-1500尾、平均规格50-75g/尾;刮食性鱼类如下:鲴鱼800-1200尾、平均规格25-50g/尾;草食性鱼类:草鱼200-250尾,平均规格500-600g/尾。The biological combination purification pond for freshwater aquaculture tail water according to claim 1, characterized in that: the filter-feeding fishes put into the fish species are as follows: 100-150 silver carp, 50-bighead carp according to each acre of water surface. 60 fish, average size 200-300g/tail; omnivorous fishes are as follows: carp 1600-2000, average size 100-150g/tail, crucian 1200-1500, average size 50-75g/tail; scraping fishes are as follows : 800-1200 carp, average size 25-50g/tail; herbivorous fish: 200-250 grass carp, average size 500-600g/tail.
  3. 根据权利要求1所述的一种淡水养殖尾水的生物组合净化塘,其特征在于:所述水生植物为凤眼莲或凤眼莲与轮叶黑藻、苦草属、狐尾藻属、金鱼藻属、眼子菜属、伊乐藻的组合;每组所述生物膜净水栅的长度为20-40m、高度0.7~1.4m,且每组所述生物膜净水栅之间的间距不小于1m。The biological combination purification pond for freshwater aquaculture tail water according to claim 1, wherein the aquatic plants are water hyacinth or water hyacinth and Hydrilla verticillata, Vallisneria, Myriophyllum, Ceratophyllum The combination of the genus, Pseudomonas, and Elodea; the length of each group of the biofilm water purification grid is 20-40m, the height is 0.7~1.4m, and the spacing between each group of the biofilm water purification grid is not Less than 1m.
  4. 根据权利要求1所述的一种淡水养殖尾水的生物组合净化塘,其特征在于:鱼种投放后经6-10个月的养殖,可进行轮捕轮放,即对达到上市规格的鱼类进行适量捕捞上市,同时继续补充投放鱼种,维持所述第一级处理单元池塘中的存鱼量大于初始投放的鱼种总重量。The biological combination purification pond for freshwater aquaculture tail water according to claim 1, characterized in that: after the fish species are put in for 6-10 months, the fish can be caught and released in rotation, that is, the fish that reach the market specifications Appropriate fishing and marketing of fish species are carried out while continuing to replenish the stocking of fish species to maintain the stock of fish in the pond of the first-level treatment unit greater than the total weight of the initially stocked fish species.
  5. 根据权利要求1所述的一种淡水养殖尾水的生物组合净化塘,其特征在于:在7-10月,每周对生长过密的水生植物进行打捞,并投放至第一级处理单元池塘,用于投喂草食性鱼类,以控制水生植物的生长密度。The biological combination purification pond for freshwater aquaculture tail water according to claim 1, characterized in that: from July to October, the densely growing aquatic plants are salvaged every week and put in the pond of the first-level treatment unit , Used to feed herbivorous fish to control the growth density of aquatic plants.
  6. 根据权利要求5所述的一种淡水养殖尾水的生物组合净化塘,其特征在于:在11月到次年3月,每周对茎叶开始发黄的水生植物进行打捞,并投放至第一级处理单元池塘,用于投喂草食性鱼类,防止衰亡茎叶在水中腐败后,氮磷释放于水体。The biological combination purification pond for freshwater aquaculture tail water according to claim 5, characterized in that: from November to March of the following year, the aquatic plants whose stems and leaves begin to turn yellow are salvaged every week, and put to the first The first-level treatment unit pond is used to feed herbivorous fishes to prevent the decay of decayed stems and leaves in the water and the release of nitrogen and phosphorus in the water body.
  7. 根据权利要求6所述的一种淡水养殖尾水的生物组合净化塘,其特征在于:于11月,补充投放一批平均尾重大于1kg的食草性鱼类,以充分摄食从第二级处理单元池塘中捞出的水生植物。The biological combination purification pond for freshwater aquaculture tail water according to claim 6, characterized in that: in November, a batch of herbivorous fishes with an average tail weight of more than 1 kg was added to fully feed from the second stage The aquatic plants picked from the pond of the processing unit.
  8. 根据权利要求1所述的一种淡水养殖尾水的生物组合净化塘,其特征在于:每年冬季用吸泥泵对第一级处理单元池塘进行清淤。The biological combined purification pond for freshwater aquaculture tail water according to claim 1, characterized in that the first-stage treatment unit pond is dredged by a mud suction pump every winter.
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114208728A (en) * 2021-11-26 2022-03-22 上海市水产研究所(上海市水产技术推广站) Method for intercropping eels in grass carp main culture pond
CN114506971A (en) * 2022-01-27 2022-05-17 乐亭县向光海水养殖场 Aquaculture tail water treatment method based on energy recycling
CN114573112A (en) * 2022-03-07 2022-06-03 河南三之缘科技有限公司 Fishery grower synthesizes and grows ecological farming systems of inner loop
CN114671564A (en) * 2021-12-11 2022-06-28 安徽蓝田农业集团有限公司 Culture tail water treatment process in aquaculture process
CN115500291A (en) * 2022-11-09 2022-12-23 贵州山至金生态农业有限公司 Mixed culture method for symbiotic grass carps of rice field and rice fish

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111422991A (en) * 2020-05-09 2020-07-17 集美大学 Biological combined purification pond for freshwater aquaculture tail water
CN113213700A (en) * 2021-04-28 2021-08-06 集美大学 Efficient phosphorus removal system for treating aquaculture tail water

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010036082A (en) * 2008-08-04 2010-02-18 Taiyo:Kk Composite circulation antibacterial bathtub system, composite circulation antibacterial warm water supply system, composite circulation antibacterial cooling tower system, composite circulation antibacterial pool system, composite circulation antibacterial water and sewerage system and composite circulation antibacterial water system for agriculture, fishing and fisheries
KR20150016170A (en) * 2013-08-02 2015-02-11 주식회사 이피에스이앤이 Water treatment apparatus
CN105309366A (en) * 2015-11-05 2016-02-10 常州市武进区水产技术推广站 Fishery industrialized circular flowing water aquaculture system and method
CN107223610A (en) * 2017-07-13 2017-10-03 安徽省农业科学院水产研究所 A kind of method for improving main foster grass carp pond culture yield and benefit
CN207061995U (en) * 2017-07-04 2018-03-02 江苏东珠景观股份有限公司 It is a kind of be combined based on plant with biomembrane it is biological floating bed
CN111422991A (en) * 2020-05-09 2020-07-17 集美大学 Biological combined purification pond for freshwater aquaculture tail water

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105941289B (en) * 2016-05-24 2019-11-22 环境保护部南京环境科学研究所 A kind of the greenhouse breeding soft-shell turtle system and breeding wastewater method of resource of high-efficiency low-pollution

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010036082A (en) * 2008-08-04 2010-02-18 Taiyo:Kk Composite circulation antibacterial bathtub system, composite circulation antibacterial warm water supply system, composite circulation antibacterial cooling tower system, composite circulation antibacterial pool system, composite circulation antibacterial water and sewerage system and composite circulation antibacterial water system for agriculture, fishing and fisheries
KR20150016170A (en) * 2013-08-02 2015-02-11 주식회사 이피에스이앤이 Water treatment apparatus
CN105309366A (en) * 2015-11-05 2016-02-10 常州市武进区水产技术推广站 Fishery industrialized circular flowing water aquaculture system and method
CN207061995U (en) * 2017-07-04 2018-03-02 江苏东珠景观股份有限公司 It is a kind of be combined based on plant with biomembrane it is biological floating bed
CN107223610A (en) * 2017-07-13 2017-10-03 安徽省农业科学院水产研究所 A kind of method for improving main foster grass carp pond culture yield and benefit
CN111422991A (en) * 2020-05-09 2020-07-17 集美大学 Biological combined purification pond for freshwater aquaculture tail water

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
DENG LAIFU, JIANG XING-LONG: "The Application and Research Progress of Bioremediation in Pond Aquaculture", OCEANOLOGIA ET LIMNOLOGIA SINICA, vol. 44, no. 5, 30 September 2013 (2013-09-30), pages 1270 - 1275, XP055865937 *
MA MIN: "Study on Phyto-Microbial Restoration of Fishing Aquacultural Wastewater", SCIENCE-ENGINEERING (A), CHINA MASTER’S THESES FULL-TEXT DATABASE, 15 October 2011 (2011-10-15), XP055865945 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114208728A (en) * 2021-11-26 2022-03-22 上海市水产研究所(上海市水产技术推广站) Method for intercropping eels in grass carp main culture pond
CN114671564A (en) * 2021-12-11 2022-06-28 安徽蓝田农业集团有限公司 Culture tail water treatment process in aquaculture process
CN114506971A (en) * 2022-01-27 2022-05-17 乐亭县向光海水养殖场 Aquaculture tail water treatment method based on energy recycling
CN114573112A (en) * 2022-03-07 2022-06-03 河南三之缘科技有限公司 Fishery grower synthesizes and grows ecological farming systems of inner loop
CN115500291A (en) * 2022-11-09 2022-12-23 贵州山至金生态农业有限公司 Mixed culture method for symbiotic grass carps of rice field and rice fish

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