CN115231710A - A kind of aquaculture tail water purification system and purification method - Google Patents
A kind of aquaculture tail water purification system and purification method Download PDFInfo
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- 238000009360 aquaculture Methods 0.000 title claims abstract description 155
- 244000144974 aquaculture Species 0.000 title claims abstract description 155
- 238000000746 purification Methods 0.000 title claims abstract description 130
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 120
- 238000000034 method Methods 0.000 title claims abstract description 15
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- 239000002028 Biomass Substances 0.000 abstract description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 abstract description 3
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 3
- 229910052698 phosphorus Inorganic materials 0.000 abstract description 3
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- 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
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F2001/007—Processes including a sedimentation step
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
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- C02F2301/046—Recirculation with an external loop
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Abstract
Description
技术领域technical field
本发明涉及水产养殖尾水净化技术领域,尤其是涉及一种水产养殖尾水净化系统及净化方法。The invention relates to the technical field of aquaculture tail water purification, in particular to an aquaculture tail water purification system and a purification method.
背景技术Background technique
中国是世界水产养殖第一大国。但是由于养殖观念的限制以及养殖技术的落后,实际生产中难以做到科学规范,导致养殖水体的污染。养殖过程中产生的污染物一方面会造成养殖动物身体免疫机能下降,易患病,影响水产品品质,另一方面外排的养殖尾水又会影响周边生态环境,引起水体的富营养化。因此,有效处理养殖池尾水成为当前池塘养殖过程中不可少的环节。China is the world's largest aquaculture country. However, due to the limitation of aquaculture concepts and the backwardness of aquaculture technology, it is difficult to achieve scientific norms in actual production, resulting in pollution of aquaculture water. On the one hand, the pollutants generated in the breeding process will cause the immune function of the farmed animals to decline, be susceptible to diseases, and affect the quality of aquatic products. Therefore, the effective treatment of the tail water of aquaculture ponds has become an indispensable link in the current pond aquaculture process.
目前水产养殖尾水净化系统主要由多级人工湿地或生物净化塘等单元组合而成。主要原理是利用基质、植物和微生物作用对污染物进行吸附或吸收。但是建设该种类型的水产养殖处理系统进行尾水处理时,往往需要利用养殖池塘面积的5%-10%。该池塘改造行为会直接减少原有养殖面积,影响渔民经济收入,因此难以被养殖户接受。除此之外,根据目前淡水池塘养殖规律,池塘尾水主要安排在冬季排放,其他季节排水量很少。因此,在非排水季节,水产养殖尾水净化系统无外部水源流入,尾水净化系统水体处于静止状态,长期无污染物输入会造成多种生物数量及活性降低,影响其在使用期的尾水处理效果。如若为了维持该系统在养殖时期的植物与微生物的活性而人为推动水体,又将会产生额外运行成本。At present, the aquaculture tail water purification system is mainly composed of units such as multi-level constructed wetlands or biological purification ponds. The main principle is to use substrates, plants and microorganisms to adsorb or absorb pollutants. However, when constructing this type of aquaculture treatment system for tail water treatment, it is often necessary to utilize 5%-10% of the area of the aquaculture pond. The pond renovation will directly reduce the original aquaculture area and affect the economic income of fishermen, so it is difficult to be accepted by farmers. In addition, according to the current law of freshwater pond culture, the pond tail water is mainly arranged to be discharged in winter, and the discharge in other seasons is very small. Therefore, in the non-drainage season, the aquaculture tail water purification system has no external water inflow, the water body of the tail water purification system is in a static state, and the long-term absence of pollutant input will cause a decrease in the number and activity of various organisms, affecting the tail water during its use period. processing effect. If the water body is artificially propelled to maintain the activity of plants and microorganisms during the cultivation period of the system, additional operating costs will be incurred.
发明内容SUMMARY OF THE INVENTION
本发明的目的在于克服上述技术不足,提出一种水产养殖尾水净化系统及净化方法,解决现有技术中水产养殖尾水净化系统减少原有养殖面积、影响渔民经济收入,且非排水季节长期无污染物输入会造成多种生物数量及活性降低、影响其在使用期的尾水处理效果的技术问题。The purpose of the present invention is to overcome the above-mentioned technical deficiencies, propose a kind of aquaculture tail water purification system and purification method, solve the problem that the aquaculture tail water purification system in the prior art reduces the original breeding area, affects the economic income of fishermen, and the non-drainage season is long-term No pollutant input will cause the reduction of the number and activity of various organisms, and affect the technical problems of the tail water treatment effect during the use period.
本发明的第一方面提供一种水产养殖尾水净化系统,包括:复合湿地净化区和循环水养殖区,循环水养殖区的后端与复合湿地净化区的前端连通,复合湿地净化区的后端与循环水养殖区的前端连通。A first aspect of the present invention provides an aquaculture tail water purification system, comprising: a composite wetland purification area and a recirculating aquaculture area, the rear end of the recirculating aquaculture area is communicated with the front end of the composite wetland purification area, and the rear end of the composite wetland purification area The end is communicated with the front end of the circulating aquaculture area.
本发明的第二方面提供一种水产养殖系统,包括本发明第一方面提供的水产养殖尾水净化系统和普通养殖区,普通养殖区的后端与复合湿地净化区的前端连通,普通养殖区的前端与复合湿地净化区的后端连通。The second aspect of the present invention provides an aquaculture system, comprising the aquaculture tail water purification system provided in the first aspect of the present invention and a common aquaculture area. The front end is communicated with the rear end of the composite wetland purification area.
本发明的第三方面提供一种水产养殖尾水净化方法,包括以下步骤:A third aspect of the present invention provides a method for purifying aquaculture tail water, comprising the following steps:
在养殖季节,普通养殖区不排水,复合湿地净化区和循环水养殖区内的水体自循环;During the breeding season, the general breeding area does not drain water, and the water in the complex wetland purification area and the circulating aquaculture area circulates itself;
在排水季节,普通养殖区排水,普通养殖区排出的尾水进入复合湿地净化区并经净化后再次进入普通养殖区。During the drainage season, the general aquaculture area is drained, and the tail water discharged from the general aquaculture area enters the compound wetland purification area and enters the ordinary aquaculture area again after purification.
与现有技术相比,本发明的有益效果包括:Compared with the prior art, the beneficial effects of the present invention include:
本发明通过在复合湿地净化区后端增设循环水养殖区,利用循环水养殖区产生的氮磷等污染物在养殖时期保持复合湿地净化区内植物和微生物的生物量及活性;在冬季尾水处理期,复合湿地净化区较高的生物活性可以完成普通养殖区养殖尾水的有效处理;此外,在养殖池塘尾水大量排放前,循环水养殖区的养殖产品可以收获上市,带来的效益可以弥补建设复合湿地净化区和循环水养殖区带来的经济损失。可见,本发明能够维持水产养殖尾水处理效果,减少构建水产养殖尾水处理系统的经济损失,保证良好的养殖水环境,实现整体水资源循环利用。By adding a recirculating aquaculture area at the rear end of the compound wetland purification area, the present invention utilizes nitrogen, phosphorus and other pollutants generated in the recirculating aquaculture area to maintain the biomass and activity of plants and microorganisms in the compound wetland purification area during the breeding period; During the treatment period, the higher biological activity of the compound wetland purification area can complete the effective treatment of the tail water of the common aquaculture area; in addition, before the tail water of the aquaculture pond is discharged in large quantities, the aquaculture products in the recirculating aquaculture area can be harvested and marketed, bringing benefits. It can make up for the economic losses caused by the construction of complex wetland purification areas and recirculating aquaculture areas. It can be seen that the present invention can maintain the effect of aquaculture tail water treatment, reduce the economic loss of constructing an aquaculture tail water treatment system, ensure a good aquaculture water environment, and realize the overall water resource recycling.
附图说明Description of drawings
图1为常规养殖季节水产养殖尾水净化系统水流循环示意图;Fig. 1 is the schematic diagram of the water flow circulation of the aquaculture tail water purification system in the conventional breeding season;
图2为冬季排水期水产养殖尾水净化系统水流循环示意图;Fig. 2 is a schematic diagram of the water flow circulation of the aquaculture tail water purification system during the winter drainage period;
图3为循环水养殖区中养殖桶、排污泵与固液分离塔一实施方式的结构示意图。FIG. 3 is a schematic structural diagram of an embodiment of a culture bucket, a sewage pump and a solid-liquid separation tower in a recirculating aquaculture area.
具体实施方式Detailed ways
为了使本发明的目的、技术方案及优点更加清楚明白,以下结合附图及实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅仅用以解释本发明,并不用于限定本发明。In order to make the objectives, technical solutions and advantages of the present invention clearer, the present invention will be further described in detail below with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are only used to explain the present invention, but not to limit the present invention.
请参阅图1-3,本发明的第一方面提供一种水产养殖尾水净化系统,包括:复合湿地净化区100和循环水养殖区200,循环水养殖区200的后端与复合湿地净化区100的前端连通,复合湿地净化区100的后端与循环水养殖区200的前端连通,以便循环水养殖区200内的水体通入到复合湿地净化区100前端,经复合湿地净化区100处理后从复合湿地净化区100后端通入循环水养殖区200的前端。循环水养殖区200需要定期把一部分水体交换或净化以保证循环水养殖区200内的盐度、碱度、pH等理化指标的稳定,以及减少氨氮等毒性物质影响养殖对象,这种水体交换是循环水养殖区200的特点,本发明正是利用这种特点,将循环水养殖区200产生的含有氮磷等污染物的水体通入到复合湿地净化区100前端,同时从复合湿地净化区100后端补充清洁水体进入循环水养殖区200。该操作一方面可以保证循环水养殖区200的水环境质量,另一方面可以通过联动循环水养殖区200及复合湿地净化区100实现养殖季节系统内的水体流通,保持养殖时期复合湿地净化区100内植物和微生物的生物量及活性;同时还能利用循环水养殖区收获的水产品减少复合湿地净化区和循环水养殖区占地带来的经济损失。1-3, a first aspect of the present invention provides an aquaculture tail water purification system, including: a complex
本发明中,本领域技术人员应当理解,复合湿地净化区100的前端或后端指复合湿地净化区100的进水端或出水端,循环水养殖区200的前端或后端指循环水养殖区200的进水端或出水端。In the present invention, those skilled in the art should understand that the front or rear end of the composite
本发明中,上述复合湿地净化区100包括多级沉淀塘区、人工湿地区、沉水植物净化区或生物刷区中的至少一种。In the present invention, the above-mentioned composite
在本发明的一些具体实施方式中,上述复合湿地净化区100包括沿循环方向依次设置的第一沉水植物净化区101、潜流人工湿地区102、生物刷区103和第二沉水植物净化区104。In some specific embodiments of the present invention, the above-mentioned composite
本发明中,上述循环水养殖区200为设施化高密度养殖区。In the present invention, the above-mentioned circulating
进一步地,上述设施化高密度养殖区包括流道养殖装置、集装箱养殖装置、圈养养殖装置中的至少一种。Further, the above-mentioned facility high-density culture area includes at least one of a channel culture device, a container culture device, and a captive culture device.
在本发明的一些具体实施方式中,上述设施化高密度养殖区包括圈养养殖装置,且圈养养殖装置包括养殖桶201、排污泵202和固液分离塔203,养殖桶201底部的排污口与排污泵202的进水口通过排污管道连通,排污泵202出水口分别与固液分离塔203和复合湿地净化区100的前端通过排污管道连通,连接处均设有阀门。进一步地,位于排污泵202与固液分离塔203间的排污管道上设置有阀门A,位于排污泵202与复合湿地净化区100的前端间的排污管道上设置有阀门B。进一步地,养殖桶201设置在水中,其上设置有进水孔,使经复合湿地净化区100净化处理后的清洁水经进水孔在液位高度差的作用下自发进入养殖桶201内。In some specific embodiments of the present invention, the above-mentioned facility high-density breeding area includes a captive breeding device, and the captive breeding device includes a
本发明中,养殖桶201、排污泵202、固液分离塔203的具体结构均为现有技术,本发明对此不作赘述。In the present invention, the specific structures of the
本发明中,循环水养殖区200的面积为水产养殖尾水净化系统总面积的15-25%,进一步为20-25%。本发明通过将循环水养殖区200的面积设计在该范围内,使循环水养殖区200产生的污染负荷能够满足复合湿地净化区100功能生物的生长需要,且不会产生新的污染。In the present invention, the area of the circulating
本发明的第二方面提供一种水产养殖系统,包括本发明第一方面提供的水产养殖尾水净化系统和普通养殖区300,普通养殖区300的后端与复合湿地净化区100的前端连通,普通养殖区300的前端与复合湿地净化区100的后端连通。The second aspect of the present invention provides an aquaculture system, comprising the aquaculture tail water purification system provided in the first aspect of the present invention and a
在本发明的一些具体实施方式中,普通养殖区300的前端通过循环水养殖区200与复合湿地净化区100的后端连通。这种设置方式,可使经过复合湿地净化区100净化后的水经循环水养殖区200进入普通养殖区300,无需额外增设沟渠或管道,还可以起到减缓水流的作用。In some specific embodiments of the present invention, the front end of the
本发明中,水产养殖尾水净化系统的面积为水产养殖系统总面积的6-10%,进一步为10%。本发明中,通过将水产养殖尾水净化系统的面积的设置在该范围内,使水产养殖尾水净化系统中的复合湿地净化区100能够充分降解普通养殖区300产生的污染负荷,且最大程度保证普通养殖区300的经济效益。In the present invention, the area of the aquaculture tail water purification system is 6-10% of the total area of the aquaculture system, further 10%. In the present invention, by setting the area of the aquaculture tail water purification system within this range, the composite
本发明中,通过设置沟渠或管道将复合湿地净化区100、循环水养殖区200以及普通养殖区300连通。In the present invention, the composite
本发明的第三方面提供一种水产养殖尾水净化方法,包括以下步骤:A third aspect of the present invention provides a method for purifying aquaculture tail water, comprising the following steps:
在养殖季节,普通养殖区300不排水,复合湿地净化区100和循环水养殖区200内的水体自循环;During the breeding season, the
在排水季节,普通养殖区300排水,普通养殖区300排出的尾水进入复合湿地净化区100并经净化后再次进入普通养殖区300。During the drainage season, the
本发明中,本领域技术人员应当理解,养殖季节和排水季节均针对普通养殖区而言,传统养殖季节一般为春夏秋三季,排水季节一般为冬季。但本领域技术人员也可根据实际情况确定养殖季节和排水季节,本发明对其不作限制。In the present invention, those skilled in the art should understand that both the breeding season and the drainage season are for common breeding areas, the traditional breeding season is generally spring, summer and autumn, and the drainage season is generally winter. However, those skilled in the art can also determine the breeding season and the drainage season according to the actual situation, which is not limited in the present invention.
本发明中,上述复合湿地净化区100和循环水养殖区200内的水体自循环具体包括:利用循环水养殖区200的排污泵202抽污,待污水变清后将清水通过排污管道送至复合湿地净化区100的前端;同时,循环水养殖区200从复合湿地净化区100的后端补充清洁水源,使水流形成自循环。进一步地,排污泵抽清水的时间为20-40min。In the present invention, the self-circulation of the water body in the above-mentioned composite
在本发明的一些优选实施方式中,普通养殖区300排出的尾水进入复合湿地净化区100并经净化后经由循环水养殖区200再次进入普通养殖区300。In some preferred embodiments of the present invention, the tail water discharged from the
本发明中,在排水季节来临前,循环水养殖区200的水产品起捕售卖。In the present invention, before the drainage season comes, the aquatic products in the
实施例Example
请参阅图1-3,以养殖池塘面积200亩为例,平均养殖水深2m,具体如下:Please refer to Figure 1-3, taking the area of 200 mu of aquaculture pond as an example, the average depth of aquaculture water is 2m, the details are as follows:
(1)构建水产养殖尾水净化系统:在养殖池塘选择20亩池塘建设复合湿地净化区100和循环水养殖区200以处理全区尾水,其中15亩作为复合湿地净化区,分别建设第一沉水植物净化区101、潜流人工湿地区102、生物刷区103和第二沉水植物净化区104;剩余5亩建设循环水养殖区200,循环水养殖区200包括养殖桶201、排污泵202和固液分离塔203,养殖桶201底部的排污口与排污泵202的进水口通过排污管道连通,排污泵202出水口分别与固液分离塔203和复合湿地净化区100的前端通过排污管道连通,连接处均设有阀门。本实施例中共架设20个圈养桶与5个固液分离塔。(1) Construction of an aquaculture tail water purification system: Select a 20-mu pond to build a complex
(2)养殖尾水净化方法:普通养殖区300和循环水养殖区200从2019年5月初起进行养殖,养殖180天(6个月),养殖对象为加州鲈。每天打开排污泵202与固液分离塔203之间的阀门A,并运行排污泵202从养殖桶201底部抽废弃物进入固液分离塔203,待排出污水变清后(每天一次,每次约3min)关闭阀门A,打开排污泵202与复合湿地净化区100之间的阀门B,排污泵202再工作30min,使养殖水流沿管道进入复合湿地净化区100的前端,同时养殖桶201内涌入经复合湿地净化区100处理后的清洁水,此时运行方式如图1和3。进入低温期(约12月,冬季),鱼类不开口,为防止鱼类体质量下降,在此之前养殖结束。循环水养殖区200的鱼产品率先上市,循环水养殖区200工作结束,此后养殖池溏的鱼陆续上市,养殖池塘逐一通过排水渠将水通入复合湿地净化区100,主要利用复合湿地净化区100净化,此后再通过进水渠将清洁水运送至各个养殖池塘,如图2。(2) Purification method of aquaculture tail water: The
在春夏秋三季(4月-11月),复合湿地净化区100的后端的氨氮和亚硝酸盐分别为0.22~2.35mg/L和0.06~0.18mg/L,循环水养殖区200氨氮和亚硝酸盐分别为0.36~3.54mg/L和0.16~0.34mg/L。冬季(11月中旬)循环水养殖区的鱼上市,半个月后各养殖池塘陆续排水,经过复合湿地净化区处理,冬季尾水可达到符合《淡水养殖尾水排放要求(征求意见稿)》(SC/T9101-2007)规定的一级标准。In spring, summer and autumn (April-November), the ammonia nitrogen and nitrite at the back end of the complex
此外,通过测产,循环水养殖区200内加州鲈平均产量可达到1t/圈养桶(养殖180天),20个圈养桶总产量可达到20t,当年(2019年)加州鲈市场价以30元/kg计,圈养系统内养殖加州鲈产值可达到60万元,去除水电、鱼药、鱼种等费用,总利润可达20万元。通过渔民走访调查,普通池塘的产量为600-1000kg/亩(养殖189天),单位面积净利润仅为7000-10000元/亩,20亩水产养殖尾水净化系统的占地面积损失最高达20万元。可见,本发明构建的循环水养殖区还可以弥补复合湿地净化区100和循环水养殖区200占地带来的经济损失。In addition, through production measurement, the average output of California perch in 200 recirculating aquaculture areas can reach 1t/captive barrel (180 days of culture), and the total output of 20 captive barrels can reach 20t. The market price of California perch in that year (2019) was 30 yuan/kg Calculated, the output value of the California sea bass in the captive system can reach 600,000 yuan, and the total profit can reach 200,000 yuan, excluding water, electricity, fish medicine, fish fingerlings and other expenses. Through the investigation of fishermen, the output of ordinary ponds is 600-1000kg/mu (189 days of breeding), the net profit per unit area is only 7,000-10,000 yuan/mu, and the area loss of the 20-mu aquaculture tail water purification system is up to 20%. million. It can be seen that the recirculating aquaculture area constructed by the present invention can also make up for the economic loss caused by the land occupation of the composite
与现有技术相比,本发明的有益效果还包括:Compared with the prior art, the beneficial effects of the present invention also include:
(1)在养殖季节,复合湿地净化区的水与普通养殖区无接触,以循环水养殖区产生的水体作为循环水带来驱动力带动整个尾水净化系统在养殖季节进行水体流转,维持甚至提高系统净化效力以备冬季使用,且弥补复合湿地净化区和循环水养殖区占用池塘面积产生的经济损失;同时,复合湿地净化区也可以看作是循环水养殖区的处理单元,该处理单元的作用主要是最大限度降解污染物;在非养殖季节,循环水养殖区不运行,整个尾水净化系统主要是复合湿地净化区发挥净化作用,该作用与普通尾水净化系统的污染物去除原理无差别,但由于本发明的复合湿地净化区一直处于运行状态,处理效果将显著优于普通尾水净化系统。(1) During the breeding season, the water in the complex wetland purification area has no contact with the ordinary breeding area, and the water produced in the recirculating aquaculture area is used as the driving force for circulating water to drive the entire tail water purification system to circulate the water during the breeding season, maintaining even Improve the purification efficiency of the system for use in winter, and make up for the economic loss caused by the pond area occupied by the composite wetland purification area and the recirculating aquaculture area; The main function is to degrade pollutants to the maximum extent; in the non-aquaculture season, the recirculating aquaculture area does not operate, and the entire tail water purification system mainly plays a purification role in the composite wetland purification area, which is similar to the pollutant removal principle of the ordinary tail water purification system. There is no difference, but since the composite wetland purification area of the present invention is always in operation, the treatment effect will be significantly better than that of the ordinary tail water purification system.
(2)普通养殖区(养殖池塘)一般在养殖过程中只有可能进行原位水环境修复(泼洒光合细菌等微生态试剂),不会异位修复,也就是把水移出来处理,如若为了维持该系统在养殖时期的植物与微生物的活性而人为推动水体,一方面会产生抽水成本的问题,另一方面养殖池塘养殖过程产生的污染物量少,对植物与微生物的活性提升作用不大,并且该设计也没有产生经济效益。(2) Ordinary aquaculture areas (aquaculture ponds) are generally only possible to perform in-situ water environment restoration (sprinkling micro-ecological reagents such as photosynthetic bacteria) during the breeding process, but not ex-situ restoration, that is, remove the water for treatment, if in order to maintain The system artificially promotes the water body due to the activity of plants and microorganisms during the breeding period. On the one hand, it will cause the problem of pumping costs. On the other hand, the amount of pollutants generated during the breeding process in the pond is small, which has little effect on the activity of plants and microorganisms. And the design is not economical either.
以上所述本发明的具体实施方式,并不构成对本发明保护范围的限定。任何根据本发明的技术构思所做出的各种其他相应的改变与变形,均应包含在本发明权利要求的保护范围内。The specific embodiments of the present invention described above do not limit the protection scope of the present invention. Any other corresponding changes and modifications made according to the technical concept of the present invention shall be included in the protection scope of the claims of the present invention.
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Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104211259A (en) * | 2014-09-16 | 2014-12-17 | 同济大学 | Multifunctional ecological purification system for large-scale circulation breeding water |
| CN112616766A (en) * | 2020-12-29 | 2021-04-09 | 华中农业大学 | Improved circulating water aquaculture system and tail water treatment method thereof |
| CN113526785A (en) * | 2021-06-04 | 2021-10-22 | 华中农业大学 | One-pond one-dam fresh water pond culture tail water treatment system |
-
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Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104211259A (en) * | 2014-09-16 | 2014-12-17 | 同济大学 | Multifunctional ecological purification system for large-scale circulation breeding water |
| CN112616766A (en) * | 2020-12-29 | 2021-04-09 | 华中农业大学 | Improved circulating water aquaculture system and tail water treatment method thereof |
| CN113526785A (en) * | 2021-06-04 | 2021-10-22 | 华中农业大学 | One-pond one-dam fresh water pond culture tail water treatment system |
Non-Patent Citations (1)
| Title |
|---|
| 何绪刚: ""池塘‘零排放’绿色高效圈养技术"", 《科学养鱼》, pages 16 * |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
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