CN207733466U - The one seed shrimp dish crop rotation ecologic breeding pool - Google Patents
The one seed shrimp dish crop rotation ecologic breeding pool Download PDFInfo
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- 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
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Abstract
Description
技术领域technical field
本实用新型属于水产养殖领域,具体涉及一种新型虾菜轮作生态养殖塘。The utility model belongs to the field of aquaculture, in particular to a novel shrimp and vegetable rotation ecological breeding pond.
背景技术Background technique
随着水产品市场需求的扩大,水产养殖以其巨大发展潜力迎合了人们对水产品不断增长的需求而获得了迅猛发展,水产养殖事业的蓬勃发展和养殖规模在不断扩大;随着水产养殖业的迅速发展,养殖面积正在逐步扩大,导致了一系列环境问题的产生,例如淡水养殖不断开发新的养殖塘所带来的土地资源利用率下降问题,虾塘底泥氮磷含量高从而常常使虾塘水质受到影响等已经成为国家和业界十分关注的问题。过多的池塘淤泥已成为近年来制约养殖产量、造成养殖的水产病暴发的主要因素, 而实施池塘清淤改造投入较大,养殖单位与个人往往难以承受。With the expansion of market demand for aquatic products, aquaculture has achieved rapid development by catering to people's growing demand for aquatic products with its huge development potential. The vigorous development of aquaculture and the continuous expansion of aquaculture scale; With the rapid development, the aquaculture area is gradually expanding, leading to a series of environmental problems, such as the decline in the utilization rate of land resources brought about by the continuous development of new aquaculture ponds for freshwater aquaculture, and the high nitrogen and phosphorus content in the bottom mud of shrimp ponds often makes the The impact on the water quality of shrimp ponds has become a matter of great concern to the country and the industry. Excessive pond silt has become the main factor restricting aquaculture production and causing outbreaks of aquatic diseases in recent years. However, the investment in pond dredging and reconstruction is often unaffordable for aquaculture units and individuals.
由于海洋自然资源的限制,水产品消费量的增长需求,必须靠养殖业的发展去满足。但是进一步扩大水养殖业受到资源与环境的限制。传统的养殖方式由于饲养密度的限制,需要大量的水源,而水源短缺已成为世界性问题。为了增加产量,提高生产效率和充分利用水源,近年来高密度集约养殖被广泛采用。池塘是人工构建的小型养殖水体,一般为人工营养型(或异养型)养殖系统。集约化池塘养殖是以投入人工饵料为特征的高密度养殖系统。调查研究表明,集约化池塘养殖的主要污染源为残饵、鱼虾的排泄物和代谢物、藻类残体与代谢物、池塘水体消毒和鱼虾治病使用的化学药物、以及外源水带入的污染物。人工饲料的投入,使得集约式养殖造成环境的污染十分严重,在淡水养殖方面,养1吨淡水鱼产生的粪便相当于20头猪的粪便量,在海水养殖方面,每生产1吨虾需要投下饲料3吨~5吨,相当于蛋白质1吨~1.3吨,利用率却只有20%左右,大量的氮流入水体中,造成养殖水域的二次污染。同时,由于这种饲养方式所涉及的废水排放量较大,水处理及污染控制都较困难。另外,由于内陆水体和近海受到工业、民用和农业污染的影响,水质变坏,影响其用于水产养殖的适用性,导致可利用水源的进一步减少。由于池塘养殖业的快速发展,养殖生产中的水环境问题也不断被认识,集约化池塘循环水健康养殖已成为重要的发展方向。Due to the limitation of marine natural resources, the growing demand for aquatic product consumption must be met by the development of aquaculture. However, further expansion of the aquaculture industry is limited by resources and the environment. Due to the limitation of stocking density, the traditional breeding method needs a lot of water, and the shortage of water has become a worldwide problem. In order to increase production, improve production efficiency and make full use of water sources, high-density intensive farming has been widely used in recent years. Ponds are artificially constructed small-scale aquaculture water bodies, generally artificial trophic (or heterotrophic) aquaculture systems. Intensive pond aquaculture is a high-density aquaculture system characterized by inputting artificial bait. Investigations and studies have shown that the main sources of pollution in intensive pond farming are residual bait, excrement and metabolites of fish and shrimp, algae residues and metabolites, chemicals used for disinfection of pond water and treatment of fish and shrimp, and the introduction of external water. pollutants. The input of artificial feed causes serious environmental pollution caused by intensive farming. In terms of freshwater aquaculture, the feces produced by raising 1 ton of freshwater fish is equivalent to the amount of feces produced by 20 pigs. In terms of mariculture, each ton of shrimp needs to be cast 3 to 5 tons of feed is equivalent to 1 to 1.3 tons of protein, but the utilization rate is only about 20%. A large amount of nitrogen flows into the water body, causing secondary pollution of the breeding waters. At the same time, due to the large amount of wastewater discharge involved in this breeding method, water treatment and pollution control are all relatively difficult. In addition, due to the impact of industrial, civil and agricultural pollution on inland water bodies and coastal waters, the water quality has deteriorated, affecting its applicability for aquaculture, resulting in a further reduction in available water sources. Due to the rapid development of the pond aquaculture industry, the water environment problems in aquaculture production are constantly being recognized, and intensive pond circulating water healthy aquaculture has become an important development direction.
发明内容Contents of the invention
本实用新型公开了一种基于新型生态养殖塘的虾菜轮作模式,包括水产养殖和蔬菜种植,二者交替进行,本实用新型“轮作”能够有效利用养殖空间,促进农业与水产业有机结合,实现“一田多用、虾菜双收”,实现小规模大效益,是一种高质、高产、高效生态种养模式;水产养殖在每年的6-9月份时间段进行,蔬菜种植在每年的10月份至次年5月份时间段进行。比如水产养殖的养殖对象是生长高峰期为6-9月份的南美白对虾,蔬菜种植的对象是冬春季栽培的西蓝花、雪里蕻和榨菜等蔬菜, 西蓝花、雪里蕻和榨菜种植区域交错分布。The utility model discloses a shrimp-vegetable rotation mode based on a new type of ecological breeding pond, which includes aquaculture and vegetable planting, and the two are carried out alternately. The "crop rotation" of the utility model can effectively use the breeding space and promote the organic combination of agriculture and aquaculture. It is a high-quality, high-yield, high-efficiency ecological farming model to achieve "one field with multiple uses, double harvest of shrimp and vegetables" and realize small-scale and large-scale benefits; aquaculture is carried out during the period from June to September each year, and vegetables are planted in the annual From October to May of the following year. For example, the target of aquaculture is Penaeus vannamei whose growth peak period is from June to September. The target of vegetable planting is broccoli, potherb mustard and mustard and other vegetables cultivated in winter and spring. The planting areas of broccoli, mustard and mustard are staggered .
一种虾菜轮作生态养殖塘,包括沉淀池、过滤池、净化池、养殖池、增氧设备;所述沉淀池与养殖池之间设有格栅;所述净化池与养殖池之间设有抽水泵;所述过滤池位于沉淀池与净化池之间;所述沉淀池与过滤池之间设有高位水口;所述过滤池与净化池之间设有低位水口;所述增氧设备位于抽水泵出水口处;所述净化池设有外接水管;所述养殖池底部设有厚度0.2~0.4m的淤泥层;所述养殖池的池埂坡比为1∶2.5;水产养殖时期,生态养殖塘呈沉淀池+过滤池+净化池+养殖池的组合模式,生态养殖塘内的水在各功能池的底部与水面的高程差的作用下,水体流动的方向为:养殖池-沉淀池-过滤池-净化池,净化池内的水在水泵的作用下被不断抽送到养殖池内,如此,生态养殖塘内的水得以不断进行循环流动,提高水体的自净能力。A shrimp-vegetable rotation ecological breeding pond, comprising a sedimentation tank, a filter tank, a purification tank, a culture tank, and oxygenation equipment; a grid is arranged between the sedimentation tank and the culture tank; a pumping tank is arranged between the purification tank and the culture tank Water pump; the filter tank is located between the sedimentation tank and the purification tank; a high water outlet is provided between the sedimentation tank and the filter tank; a low water outlet is provided between the filter tank and the purification tank; the aeration equipment is located at the outlet of the pump The purification pond is provided with an external water pipe; the bottom of the culture pond is provided with a silt layer with a thickness of 0.2-0.4m; the slope ratio of the pond in the culture pond is 1:2.5; The combination mode of pond + filter pond + purification pond + breeding pond, the water in the ecological breeding pond is under the effect of the elevation difference between the bottom of each functional pond and the water surface, the direction of water flow is: breeding pond-sedimentation pond-filtering pond-purification The water in the purification pond is continuously pumped into the aquaculture pond under the action of the water pump, so that the water in the ecological aquaculture pond can circulate continuously and improve the self-purification ability of the water body.
本实用新型中,池塘一分为二,其中约15%用于沉淀池、过滤池、净化池实现循环水净化处理,另外85%的养殖池部分用于虾蟹鱼类养殖,同时沉淀池、过滤池、净化池可作为育苗区,养殖池可作为种植区;优选沉淀池的面积为养殖池面积的4%,过滤池的面积为养殖池面积的8%,净化池面积为养殖池面积的6%,中间分隔比如堆砌一道水坝。池塘养殖水体通过溢流的方式,经格栅拦截对虾后,进入沉淀系统,在沉淀系统中沉淀部分泥沙后,自流至过滤系统,当进水自上而下流经滤层时,水中的悬浮物及粘胶质颗粒被去除,从而使水的浊度降低,再进入水质净化系统,进一步清除水中氨氮、亚硝态氮等可溶性有毒物质,形成一个内循环系统。In the utility model, the pond is divided into two, about 15% of which are used for sedimentation tanks, filter tanks, and purification pools to realize circulating water purification treatment, and the other 85% of the breeding pools are used for shrimp, crab and fish farming. Filtration pond and purification pond can be used as nursery area, and culture pond can be used as planting district; The area of preferred settling pond is 4% of culture pond area, and the area of filter pond is 8% of culture pond area, and purification pond area is 4% of culture pond area. 6%, the middle partition is like building a dam. The pond aquaculture water body passes through the overflow method, intercepts the prawns through the grille, and then enters the sedimentation system. After some sediment is deposited in the sedimentation system, it flows to the filtration system by itself. When the incoming water flows through the filter layer from top to bottom, the suspension in the water Substances and viscose particles are removed, thereby reducing the turbidity of the water, and then enter the water purification system to further remove ammonia nitrogen, nitrite nitrogen and other soluble toxic substances in the water, forming an internal circulation system.
本实用新型沉淀池高效沉淀结构、过滤系统高效截污设计、水质净化系统与养殖池塘面积比例研究的结合实现池塘生态养殖系统水体内循环,既满足水量需求,更主要自净化水体;形成池塘养殖水域环境内循环生态化调控及改善技术集成,实现养殖水的持续利用和养殖废物“零排放”。The combination of the high-efficiency sedimentation structure of the sedimentation tank of the utility model, the high-efficiency sewage interception design of the filtration system, the water quality purification system and the research on the area ratio of the aquaculture pond realizes the water circulation in the pond ecological aquaculture system, which not only meets the water demand, but also mainly self-purifies the water body; forms a pond aquaculture The ecological regulation of the internal cycle of the water environment and the integration of improved technologies can realize the sustainable use of aquaculture water and "zero discharge" of aquaculture waste.
本实用新型中,所述沉淀池设有第一隔板、第二隔板、第三隔板;所述第一隔板、第二隔板、第三隔板依次设置;所述第一隔板位于格栅处;所述第一隔板底面高于沉淀池底面;所述第二隔板顶面低于沉淀池顶面;所述第三隔板底面高于沉淀池底面,从而可以缓和水流,达到最佳沉淀效果;所述格栅的面积为格栅所在的沉淀池侧边面积的60%,可以满足养殖水体需求,结合沉淀、过滤、净化设计,达到水量与净化效果的双赢。优选所述第一隔板位于第二隔板的一侧设有斜网;所述斜网与第一隔板的夹角为30度,可以减弱水冲击力,防止泥沙搅动,还可以阻拦一些絮状轻质杂物;养殖水体中泥沙含量较高,可在沉淀池内进行沉淀,防止或延缓后续过滤系统的堵塞,同时对引水中的氮、磷以及其他有机污染物也有一定的去除作用。In the utility model, the sedimentation tank is provided with a first partition, a second partition, and a third partition; the first partition, the second partition, and the third partition are arranged in sequence; the first partition The plate is located at the grid; the bottom surface of the first partition is higher than the bottom surface of the sedimentation tank; the top surface of the second partition is lower than the top surface of the sedimentation tank; the bottom surface of the third partition is higher than the bottom surface of the sedimentation tank, so that the The water flow achieves the best sedimentation effect; the area of the grille is 60% of the side area of the sedimentation tank where the grille is located, which can meet the needs of aquaculture water body, combined with sedimentation, filtration, and purification design, to achieve a win-win situation of water volume and purification effect. Preferably, the first partition is provided with an inclined net on one side of the second partition; the angle between the inclined net and the first partition is 30 degrees, which can weaken the impact force of water, prevent sediment agitation, and block Some flocculent light impurities; the sediment content in the aquaculture water is relatively high, which can be deposited in the sedimentation tank to prevent or delay the blockage of the subsequent filtration system, and at the same time, nitrogen, phosphorus and other organic pollutants in the diversion water can also be removed to a certain extent effect.
本实用新型中,所述过滤池自上而下依次设置引流板、滤网、无机滤料层、微生物微球层;所述引流板倾斜设置;所述引流板位置高的一端位于高位水口下方;所述引流板设有复数个倒圆台型通孔提高水动力,从而可以避免高位水口排出的水仅在出口处流下,利用引流板可以激活整个过滤系统的能力;所述低位水口位于微生物微球层下方,优选所述引流板设有侧壁;本系统内的过滤系统采用无机物、微生物配合过滤系统,当进水自上而下流经滤层时,水中的悬浮物及粘胶质颗粒被去除,从而使水的浊度降低,而后有机物被除去,具有设备结构简单、处理流量大、反冲次数少、过滤效率高、阻力小、操作维修方便等特点。In the utility model, the filter pool is provided with a drainage plate, a filter screen, an inorganic filter material layer, and a microbial microsphere layer sequentially from top to bottom; the drainage plate is arranged obliquely; the high end of the drainage plate is located below the high water outlet ; The diversion plate is provided with a plurality of rounded platform-shaped through holes to improve the hydrodynamic force, thereby preventing the water discharged from the high-level nozzle from flowing down only at the outlet, and the ability of the entire filtration system can be activated by using the diversion plate; Below the ball layer, it is preferable that the drainage plate is provided with a side wall; the filtration system in this system adopts an inorganic matter and a microbial filter system, and when the incoming water flows through the filter layer from top to bottom, the suspended solids and viscose particles in the water It is removed, so that the turbidity of the water is reduced, and then the organic matter is removed. It has the characteristics of simple equipment structure, large processing flow, less recoil times, high filtration efficiency, small resistance, and convenient operation and maintenance.
本实用新型中,所述养殖池底部设有厚度0.2~0.4m的淤泥层,优选淤泥层厚度0.3 m,优选养殖池池深2 m,池埂坡比1 :2.5,蔬菜种植时期,将养殖塘内的水排干,塘底不渗不漏,池坡土质较硬,进排水方便,可以清除过多淤泥,整平池底。In the utility model, the bottom of the culture pond is provided with a silt layer with a thickness of 0.2~0.4m, preferably the thickness of the silt layer is 0.3m, the depth of the preferably culture pond is 2m, and the slope ratio of the pond is 1:2.5. The water in the pond is drained, and the bottom of the pond is impermeable. The soil on the slope of the pond is relatively hard, and the drainage is convenient. Excessive silt can be removed and the bottom of the pond can be leveled.
本实用新型中,养殖池底部设有周沟与排水沟,优选周沟的沟宽0.5 m、深0.5 m,所述排水沟的沟宽0.3 m、深0.2 m,限定与优选水利参数便于蔬菜种植期间排水与灌溉。所述排水沟与周沟相通,优选排水沟为“井”字形结构,从而养殖池养殖完后,排水整平畦面可以作为蔬菜种植田,同时沉淀池、过滤池、净化池直接作为育苗田;比如水产养殖时期,南美白对虾虾苗投放量为4万尾/亩,蔬菜种植时期,播种方式为15g/亩,合理密植按60X40厘米组合移栽,每亩密度2700~3000株。养殖水位根据水温变化而定,掌握“春浅夏满”的原则,春季水深保持0.6~0.8 m,有利于水温快速增高,促进南美白对虾摄食生长;夏季水温较高时,水深控制在1~1.2 m,防止水温过高,避免形成“老头虾”。In the utility model, the bottom of the breeding pond is provided with a peripheral ditch and a drainage ditch, preferably the ditch width of the peripheral ditch is 0.5 m, and the depth is 0.5 m. The ditch width of the drainage ditch is 0.3 m, and the depth is 0.2 m. Drainage and irrigation during planting. The drainage ditch communicates with the surrounding ditch, and the drainage ditch is preferably in the shape of a "well", so that after the breeding pond is cultivated, the drainage and leveling surface can be used as a vegetable planting field, and at the same time, the sedimentation tank, filtration tank, and purification tank are directly used as seedling cultivation fields. For example, during the aquaculture period, the amount of Penaeus vannamei seedlings was 40,000/mu, and during the vegetable planting period, the sowing method was 15g/mu, and the reasonable dense planting was transplanted in a combination of 60X40 cm, with a density of 2700~3000 plants per mu. The water level for aquaculture is determined according to changes in water temperature, and the principle of "shallow spring and full summer" is mastered. The water depth in spring is kept at 0.6-0.8 m, which is conducive to the rapid increase of water temperature and the growth of Penaeus vannamei. When the water temperature is high in summer, the water depth is controlled at 1-0.8 m. 1.2 m to prevent the water temperature from being too high and avoid the formation of "old man shrimp".
本实用新型中,所述沉淀池设有水体氧含量检测设备;所述养殖池设置水温检测设备;所述净化池设有水体有机元素检测设备,设备安装以及购买使用属于现有技术,更主要的是,通过水体氧含量检测设备的定位设置可以准确的检测养殖池内的氧容量情况,为增氧提供依据,通过水温检测设备的定位设置可以准确的检测养殖池温度,给予养殖合理的条件,水体有机元素检测则直观告诉塘主自循环效果。In the utility model, the sedimentation tank is provided with water oxygen content detection equipment; the breeding pond is provided with water temperature detection equipment; The most important thing is that the oxygen capacity in the breeding pond can be accurately detected through the positioning setting of the water oxygen content detection equipment, which provides a basis for oxygenation, and the temperature of the breeding pond can be accurately detected through the positioning setting of the water temperature detection equipment, giving reasonable conditions for breeding. The detection of organic elements in the water directly tells the pond owner the self-circulation effect.
本实用新型在有效控制外源污染的同时,通过调控水生生态系统结构,恢复自然、健康与稳定的水生生态系统功能,增强对外界干扰的缓冲能力,使水生生态系统处于良性与可持续循环状态,是水环境治理的最佳途径。养殖主要污染物为有机物、N、P、S 等植物营养性物质和转化形成的毒性物质,污染物按形态可分为有机悬浮态、有机胶体态和溶解态物质。污染的主要表现形式为池塘中耗氧物质的增多引起耗氧量增大,进而引起池塘水体缺氧从而导致缺氧条件下水生动物毒性物质的形成等,造成养殖池塘水体环境质量的恶化。本实用新型提供的养殖系统是对渔业捕捞不足的补充,也是水域生物资源保护和可持续发展水产养殖业的需要,可以成为未来养殖的趋势。有以下几个主要优点:一是节水省地,由于系统本身采用辅助增氧和水处理过程,循环系统能够采用高密度养殖,并反复使用同一水体,既减少了水的用量,也提高了地面的利用率;二是对环境影响小,由于循环系统本身具有对鱼的排泄物的处理能力,使这些排泄物对外面环境的影响减小;另外循环水系统大大降低了废水的排放量,便于排出的废水的处理与管理。在循环水处理水质净化技术中,本实用新型利用生态修复技术处理水产养殖废水与传统的物理修复和化学修复相比,具有费用低、耗时短、净化彻底、不易产生二次污染、不危害养殖功能、不破坏生态平衡等诸多优点。本实用新型所述净化池自上而下依次设置光催化多孔陶瓷板、水生植物层、鹅卵石层;所述低位水口位于鹅卵石层上方;所述抽水泵的进水口位于光催化多孔陶瓷板上方,利用生态系统中物理、化学和生物的三重协同作用,通过过滤、吸附、沉淀、植物吸收和微生物分解等来实现对污水的高度净化,特别适用于一个水产养殖系统内部的生物修复,能够适应于任何环境。结果表明,净化后水质中氨氮浓度小于0.4mg/L,出水BOD去除率为62%,治理效果十分显著;连续6个月的试验结束后,虾的生物量增加3倍。While effectively controlling external source pollution, the utility model restores natural, healthy and stable aquatic ecosystem functions by regulating the structure of the aquatic ecosystem, enhances the buffering capacity for external disturbances, and keeps the aquatic ecosystem in a benign and sustainable cycle state , is the best way to manage the water environment. The main pollutants in aquaculture are organic matter, N, P, S and other plant nutrient substances and toxic substances formed by transformation. Pollutants can be divided into organic suspended state, organic colloidal state and dissolved state substances according to their forms. The main form of pollution is that the increase of oxygen-consuming substances in the pond leads to the increase of oxygen consumption, which in turn causes the hypoxia of the pond water, which leads to the formation of toxic substances of aquatic animals under anoxic conditions, etc., resulting in the deterioration of the environmental quality of the aquaculture pond. The aquaculture system provided by the utility model is a supplement to the lack of fishery catch, and is also a need for the protection of biological resources in water areas and the sustainable development of aquaculture industry, and can become the trend of future aquaculture. It has the following main advantages: First, it saves water and land. Since the system itself adopts auxiliary oxygenation and water treatment processes, the circulation system can adopt high-density cultivation and use the same water body repeatedly, which not only reduces water consumption, but also improves The utilization rate of the ground; the second is that the impact on the environment is small, because the circulation system itself has the ability to process fish excrement, so that the impact of these excrement on the external environment is reduced; in addition, the circulating water system greatly reduces the discharge of waste water, Facilitate the treatment and management of discharged wastewater. In the circulating water treatment water quality purification technology, the utility model uses the ecological restoration technology to treat aquaculture wastewater, compared with the traditional physical restoration and chemical restoration, it has the advantages of low cost, short time-consuming, thorough purification, less likely to produce secondary pollution, and no harm There are many advantages such as breeding function and not destroying the ecological balance. The purification pool of the utility model is provided with a photocatalytic porous ceramic plate, an aquatic plant layer, and a pebble layer sequentially from top to bottom; the low water outlet is located above the pebble layer; the water inlet of the pump is located above the photocatalytic porous ceramic plate, Utilize the triple synergy of physics, chemistry and biology in the ecosystem to achieve a high degree of purification of sewage through filtration, adsorption, precipitation, plant absorption and microbial decomposition. It is especially suitable for bioremediation within an aquaculture system and can be adapted to any environment. The results showed that the concentration of ammonia nitrogen in the purified water was less than 0.4 mg/L, and the removal rate of BOD in the effluent was 62%, and the treatment effect was very significant; after the end of the 6-month test, the biomass of shrimp increased by 3 times.
本实用新型中,所述沉淀池为长方形结构,利于沉淀与设计安装隔板;所述沉淀池的底面低于养殖池的底面;所述过滤池的底面高于养殖池的底面;所述净化池的底面低于过滤池的底面,净化池位于养殖塘的拐角处,与沉淀池中间隔过滤池相对,净化池无出水口,通过水泵,将池内清水输送到养殖池内,形成养水体自循环,提高生态养殖塘的水体自净能力;优选所述高位水口设有高位水口塞,可以对水循环进行控制。本实用新型的净化池设有水流管,可接河水,经常冲水,保持水质“肥、活、嫩、爽”;水产养殖时期,投饵施肥以配合饲料为主,按照“四定四看”投饵原则进行科学投饵,“四定”:定质、定量、定时、定点(多点);“四看”:看天气、看摄食情况、看气温、看水温。In the utility model, the sedimentation tank is a rectangular structure, which is beneficial to sedimentation and the design and installation of partitions; the bottom surface of the sedimentation tank is lower than the bottom surface of the culture pond; the bottom surface of the filter tank is higher than the bottom surface of the culture pond; the purification The bottom of the pool is lower than the bottom of the filter tank, and the purification tank is located at the corner of the breeding pond, opposite to the filter tank in the middle of the sedimentation tank. The purification tank has no water outlet, and the clear water in the tank is transported to the breeding tank through a water pump to form a self-circulation of the breeding water body. , improve the self-purification ability of the water body of the ecological breeding pond; preferably, the high-level nozzle is provided with a high-level nozzle plug, which can control the water cycle. The purification tank of the utility model is provided with a water flow pipe, which can be connected to river water and flushed frequently to keep the water quality "fat, lively, tender and refreshing"; "The principle of feeding is scientific feeding, "four determinations": qualitative, quantitative, timing, and fixed point (multiple points); "four observations": look at the weather, look at the feeding situation, look at the temperature, and look at the water temperature.
附图说明Description of drawings
图1为实施例一虾菜轮作生态养殖塘的结构示意图;Fig. 1 is the structural representation of embodiment one shrimp-vegetable rotation ecological cultivation pond;
图2为实施例一沉淀池、过滤池、净化池的结构示意图;Fig. 2 is the structural representation of embodiment one settling pond, filter pond, purifying pond;
图3为实施例一过滤池、净化池的结构示意图;Fig. 3 is the structural representation of embodiment one filter tank, purification tank;
图4为实施例一倒圆台型通孔的结构示意图;FIG. 4 is a schematic structural view of a rounded truncated through hole in Embodiment 1;
其中,沉淀池1、过滤池2、净化池3、养殖池4、增氧设备5、格栅6、抽水泵7、外接水管8、第一隔板11、第二隔板12、第三隔板13、高位水口21、低位水口22、引流板23、滤网24、无机滤料层25、微生物微球层26、倒圆台型通孔27、光催化多孔陶瓷板31、水生植物层32、鹅卵石层33、淤泥层41、周沟42、排水沟43。Among them, sedimentation tank 1, filter tank 2, purification tank 3, culture tank 4, aeration equipment 5, grid 6, water pump 7, external water pipe 8, first partition 11, second partition 12, third partition Plate 13, high nozzle 21, low nozzle 22, drainage plate 23, filter screen 24, inorganic filter material layer 25, microbial microsphere layer 26, rounded table-shaped through hole 27, photocatalytic porous ceramic plate 31, aquatic plant layer 32, Cobblestone layer 33, silt layer 41, surrounding ditch 42, drainage ditch 43.
具体实施方式Detailed ways
实施例一Embodiment one
一种虾菜轮作生态养殖塘,包括沉淀池1、过滤池2、净化池3、养殖池4、增氧设备5;所述沉淀池与养殖池之间设有格栅6;所述净化池与养殖池之间设有抽水泵7;所述过滤池位于沉淀池与净化池之间;所述沉淀池设有第一隔板11、第二隔板12、第三隔板13;所述第一隔板、第二隔板、第三隔板依次设置;所述第一隔板位于格栅处;所述第一隔板底面高于沉淀池底面;所述第二隔板顶面低于沉淀池顶面;所述第三隔板底面高于沉淀池底面,从而形成水流道;所述格栅的面积为格栅所在的沉淀池侧边面积的60%;所述沉淀池与过滤池之间设有高位水口21,所述高位水口设有高位水口塞,用于堵住水口,为常规制作部件,附图没有表示;所述过滤池与净化池之间设有低位水口22;所述净化池自上而下依次设置光催化多孔陶瓷板31、水生植物层32、鹅卵石层33;所述低位水口位于鹅卵石层上方;所述抽水泵的进水口位于光催化多孔陶瓷板上方;所述过滤池自上而下依次设置引流板23、滤网24、无机滤料层25、微生物微球层26;所述引流板倾斜设置;所述引流板位置高的一端位于高位水口下方;所述引流板设有复数个倒圆台型通孔27;所述低位水口位于微生物微球层下方;所述增氧设备位于抽水泵出水口处;所述净化池设有外接水管8;所述养殖池底部设有厚度0.3m的淤泥层41;所述养殖池的池埂坡比为1∶2.5;所述养殖池的底部设有周沟42与排水沟43;所述周沟的沟宽为0.5 m、深为0.5 m;所述排水沟的沟宽为0.3 m、深为0.2 m。A shrimp vegetable rotation ecological culture pond, comprising a sedimentation pond 1, a filter pond 2, a purification pond 3, a cultivation pond 4, and an aeration device 5; a grid 6 is provided between the sedimentation pond and the cultivation pond; the purification pond and the A water pump 7 is provided between the breeding ponds; the filter tank is located between the sedimentation tank and the purification tank; the sedimentation tank is provided with a first partition 11, a second partition 12, a third partition 13; the first partition plate, the second partition, and the third partition are arranged in sequence; the first partition is located at the grid; the bottom surface of the first partition is higher than the bottom surface of the sedimentation tank; the top surface of the second partition is lower than the sedimentation tank Top surface; the bottom surface of the third partition is higher than the bottom surface of the sedimentation tank, thereby forming a water flow channel; the area of the grid is 60% of the side area of the sedimentation tank where the grid is located; There is a high-level nozzle 21, and the high-level nozzle is provided with a high-level nozzle plug, which is used to block the nozzle. It is a conventional production part, and the accompanying drawings do not represent it; a low-level nozzle 22 is provided between the filter tank and the purification tank; A photocatalytic porous ceramic plate 31, an aquatic plant layer 32, and a pebble layer 33 are sequentially arranged from top to bottom; A drainage plate 23, a filter screen 24, an inorganic filter material layer 25, and a microbial microsphere layer 26 are sequentially arranged from top to bottom; There are a plurality of rounded platform-shaped through holes 27; the low water outlet is located below the microbial microsphere layer; the aeration equipment is located at the water outlet of the water pump; the purification tank is provided with an external water pipe 8; A silt layer 41 with a thickness of 0.3m; the pond ridge slope ratio of the culture pond is 1: 2.5; the bottom of the culture pond is provided with a surrounding ditch 42 and a drainage ditch 43; the width of the surrounding ditch is 0.5 m, deep 0.5 m; the width of the drainage ditch is 0.3 m and the depth is 0.2 m.
所述沉淀池为长方形结构;所述沉淀池的底面低于养殖池的底面;所述过滤池的底面高于养殖池的底面;所述净化池的底面低于过滤池的底面。所述沉淀池的面积为养殖池面积的4%;所述过滤池的面积为养殖池面积的8%;所述净化池面积为养殖池面积的6%。本实用新型公开后,部件的安装属于常识,比如挖沟、做坡等。The sedimentation tank has a rectangular structure; the bottom of the sedimentation tank is lower than the bottom of the culture tank; the bottom of the filter tank is higher than the bottom of the culture tank; the bottom of the purification tank is lower than the bottom of the filter tank. The area of the sedimentation tank is 4% of the area of the culture pond; the area of the filter tank is 8% of the area of the culture pond; the area of the purification pond is 6% of the area of the culture pond. After the utility model is disclosed, the installation of parts belongs to common sense, such as digging trenches, making slopes and the like.
实施例二Embodiment two
在实施例一的基础上,根据现有安装方法,所述沉淀池安装水体氧含量检测设备;所述养殖池安装水温检测设备;所述净化池安装水体有机元素检测设备。通过水体氧含量检测设备的定位设置可以准确的检测养殖池内的氧容量情况,为增氧提供依据,通过水温检测设备的定位设置可以准确的检测养殖池温度,给予养殖合理的条件,水体有机元素检测则直观告诉塘主自循环效果。On the basis of Embodiment 1, according to the existing installation method, the sedimentation tank is equipped with water body oxygen content detection equipment; the breeding pond is equipped with water temperature detection equipment; the purification tank is equipped with water body organic element detection equipment. Through the positioning setting of the water body oxygen content detection equipment, the oxygen capacity in the breeding pond can be accurately detected, providing a basis for oxygenation, and through the positioning setting of the water temperature detection equipment, the temperature of the breeding pond can be accurately detected, giving reasonable conditions for breeding, and organic elements in the water body The detection intuitively tells the pond owner the self-circulation effect.
实施例三Embodiment Three
在实施例一的基础上,根据现有安装方法,所述第一隔板位于第二隔板的一侧设有斜网;所述斜网与第一隔板的夹角为30度,可以提升沉降效果;引流板设有侧壁,提高水流效果。On the basis of Embodiment 1, according to the existing installation method, the first partition is provided with an inclined net on one side of the second partition; the angle between the inclined net and the first partition is 30 degrees, which can be Improve the settlement effect; the diversion plate is equipped with side walls to improve the water flow effect.
完成虾菜轮作池塘的改造工作,60亩滩涂湿地挖成4个塘,每个塘14亩,和一片4亩的试验区;分析虾塘底泥成分,参照西蓝花、雪里蕻和榨菜等菜的生长所需的条件,进行相关底泥改性和底泥堆积菜地高度实验;完成相关设备采购和轮作区水利条件规划工作。Completed the transformation of shrimp and vegetable rotation ponds, dug 60 mu tidal wetland into 4 ponds, each pond 14 mu, and a 4 mu test area; analyzed the composition of shrimp pond bottom mud, referring to broccoli, potherb mustard and pickled mustard and other vegetables The conditions required for the growth of the plant, conduct relevant sediment modification and sediment accumulation vegetable field height experiments; complete the procurement of relevant equipment and the planning of water conservancy conditions in the crop rotation area.
养殖塘改造工程全部完工并各区域贯通,便于区域化管理;虾苗的投放前对鱼塘的清理和消毒等准备工作,然后进行水质调理。养殖塘改造和相关措施准备妥当。The breeding pond renovation project has been completed and all areas have been connected to facilitate regional management; before the shrimp seedlings are put in, the fish ponds are cleaned and disinfected, and then the water quality is adjusted. The transformation of breeding ponds and related measures are well prepared.
06月,投放虾苗,投放密度为:8万尾/亩;07月至08月,南美白对虾的生态养殖;09月至11月,南美白对虾轮捕上市。从9 月1 日开始对螯虾进行捕大留小销售,11月20 日开始干塘,将所有南美白对虾全部上市,共销售南美白对虾56000kg、总实现销售额102万元。In June, shrimp seedlings were put in, and the stocking density was: 80,000 tails/mu; from July to August, the ecological breeding of Penaeus vannamei was carried out; from September to November, the vannamei shrimp was caught in rotation and listed. From September 1st, the crayfish was caught and sold, and on November 20th, the ponds were dried, and all the vannamei were listed. A total of 56,000kg of vannamei were sold, with a total sales of 1.02 million yuan.
菜苗孕育,蔬菜种植时期,播种密度为15g/亩。12月至次年03月,合理密植按60X40厘米组合移栽,每亩密度2700~3000株。西蓝花、雪里蕻和榨菜等菜的种植。从次年3 月份初,开始采收西蓝花、雪里蕻和榨菜,到4 月采收结束,56亩菜田共出售水芹西蓝花、雪里蕻和榨菜约90000kg,销售额为18万元。这样,西蓝花、雪里蕻和榨菜和南美白对虾轮作试验塘口56亩平均产值2.14万元,相比较单独养殖南美白对虾而言,不仅平均产值增长率达15%,且有效降低了养殖塘底泥的有机质含量。Vegetable seedlings are gestated, and during vegetable planting, the sowing density is 15g/mu. From December to March of the next year, the reasonable dense planting should be transplanted in a combination of 60X40 cm, with a density of 2700~3000 plants per mu. The cultivation of vegetables such as broccoli, potherb mustard and mustard. From the beginning of March of the following year, broccoli, potherb mustard and mustard began to be harvested. By the end of the harvest in April, a total of 90,000 kg of cress broccoli, mustard and mustard were sold in the 56-acre vegetable field, with a sales volume of 180,000 yuan. In this way, the average output value of broccoli, potherb mustard, mustard and Penaeus vannamei in 56 mu of ponds in the rotation experiment was 21,400 yuan. Compared with the cultivation of Penaeus vannamei alone, not only the average output value growth rate reached 15%, but also effectively reduced the cost of breeding ponds. The organic matter content of the sediment.
建立30亩的海水养殖池塘及30亩的淡水养殖池塘面积的滨海池塘高效液氧增氧及内循环水净化技术集成养殖系统的示范工程,并连续运行6个月以上,监测水质状态和虾蟹鱼类的生长状况,并对该转型升级关键技术集成进行总结,形成技术参数推广应用。可以通过本实用新型养殖池塘生态设计来建立合理的生态结构和物质输运过程,从而实现控制养殖污染和生产健康水产品的目标;本实用新型采用水产/蔬菜养殖池塘与循环净水环保设施同体设计思路,通过新型水产养殖池塘的结构创新设计和水体运动方式调控,来实现池塘养殖水体循环净化、资源再生利用、滩涂生态友好、零排放、以及绿色水产品生产等功能,优良的水质既保证了水产养殖产量和规模的扩大,同时满足了健康水产养殖和环境保护的要求;结果表明,净化后水质中氨氮浓度小于0.4mg/L,出水BOD去除率为62%,治理效果十分显著;连续6个月的试验结束后,虾的生物量增加3倍。Establish a 30-acre marine aquaculture pond and a 30-mu freshwater aquaculture pond area coastal pond high-efficiency liquid oxygen aeration and internal circulation water purification technology integrated breeding system demonstration project, and run continuously for more than 6 months to monitor water quality and shrimp and crab The growth status of fish, and summarize the key technology integration of the transformation and upgrading, and form technical parameters for promotion and application. A reasonable ecological structure and material transportation process can be established through the ecological design of the aquaculture pond of the utility model, thereby realizing the goal of controlling aquaculture pollution and producing healthy aquatic products; The design idea, through the structural innovation design of the new aquaculture pond and the regulation of the water body movement mode, realizes the functions of pond aquaculture water circulation and purification, resource regeneration, tidal flat eco-friendliness, zero discharge, and green aquatic product production. Excellent water quality guarantees The expansion of aquaculture production and scale, while meeting the requirements of healthy aquaculture and environmental protection; the results show that the concentration of ammonia nitrogen in the purified water is less than 0.4mg/L, the removal rate of BOD in the effluent is 62%, and the treatment effect is very significant; continuous At the end of the 6-month trial, the biomass of the shrimp increased three-fold.
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| CN113273482A (en) * | 2021-04-27 | 2021-08-20 | 刘凯 | Biological autonomous regulation based environment-friendly treatment method for water quality of peroxide |
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| CN111248128B (en) * | 2020-03-10 | 2021-12-14 | 中国科学院南京地理与湖泊研究所 | External circulation freshwater shrimp breeding method |
| CN113273482A (en) * | 2021-04-27 | 2021-08-20 | 刘凯 | Biological autonomous regulation based environment-friendly treatment method for water quality of peroxide |
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